Reissuance of Nationwide Permits, 11092-11198 [E7-3960]
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11092
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Notices
DEPARTMENT OF DEFENSE
Department of the Army, Corps of
Engineers
[ZRIN 0710–ZA02]
Reissuance of Nationwide Permits
Army Corps of Engineers, DoD.
Final notice.
AGENCY:
ACTION:
SUMMARY: The U.S. Army Corps of
Engineers (Corps) is reissuing all
existing nationwide permits (NWPs),
general conditions, and definitions,
with some modifications. The Corps is
also issuing six new NWPs, two new
general conditions, and 13 new
definitions. The effective date for the
new and reissued NWPs will be March
19, 2007. These NWPs will expire on
March 18, 2012. The NWPs will protect
the aquatic environment and the public
interest while effectively authorizing
activities that have minimal individual
and cumulative adverse effects on the
aquatic environment.
DATES: The NWPs and general
conditions will become effective on
March 19, 2007.
ADDRESSES: U.S. Army Corps of
Engineers, Attn: CECW–CO, 441 G
Street NW., Washington, DC 20314–
1000.
Mr.
David Olson at 202–761–4922 or by email at david.b.olson@usace.army.mil or
access the U.S. Army Corps of Engineers
Regulatory Home Page at https://
www.usace.army.mil/inet/functions/cw/
cecwo/reg/.
SUPPLEMENTARY INFORMATION:
FOR FURTHER INFORMATION CONTACT:
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Background
In the September 26, 2006, issue of
the Federal Register (71 FR 56258), the
U.S. Army Corps of Engineers (Corps)
published its proposal to reissue 43
existing nationwide permits (NWPs) and
issue six new NWPs. The Corps also
proposed to reissue its general
conditions and add one new general
condition.
The Corps proposal is intended to
simplify the NWP program while
continuing to provide environmental
protection, by ensuring that the NWPs
authorize only those activities that have
minimal individual and cumulative
adverse effects on the aquatic
environment and satisfy other public
interest factors.
As a result of the comments received
in response to the September 26, 2006,
proposal, we have made a number of
changes to the NWPs, general
conditions, and definitions to further
clarify the permits, facilitate their
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administration, and strengthen
environmental protection. These
changes are discussed in the preamble.
The Corps is reissuing the 43 existing
NWPs, issuing six new NWPs, reissuing
26 existing general conditions, and
issuing one new general condition. The
Corps is also reissuing many of the NWP
definitions, and providing 13 new
definitions. The effective date for these
NWPs, general conditions, and
definitions is March 19, 2007. These
NWPs, general conditions, and
definitions expire on March 18, 2012.
While the Administrative Procedure
Act requires a substantive rule to be
published in the Federal Register at
least 30 days before its effective date,
exceptions to this requirement can be
made for good cause (5 U.S.C.
553(d)(3)). We are utilizing this good
cause exception to reduce hardships on
the regulated public.
Grandfather Provision for Expiring
NWPs
In accordance with 33 CFR 330.6(b),
activities authorized by the current
NWPs issued on January 15, 2002, that
have commenced or are under contract
to commence by March 18, 2007, will
have until March 18, 2008, to complete
the activity under the terms and
conditions of the current NWPs.
Clean Water Act Section 401 Water
Quality Certifications (WQC) and
Coastal Zone Management Act (CZMA)
Consistency Determinations
In the September 26, 2006, Federal
Register notice and concurrent with
letters from Corps Districts to the
appropriate state agencies, the Corps
requested initial 401 certifications and
CZM consistency determinations. This
began the Clean Water Act section 401
water quality certification (WQC) and
Coastal Zone Management Act (CZMA)
consistency determination processes.
Today’s Federal Register notice
begins the 60-day period for states,
Indian Tribes, and EPA to complete
their WQC process for the NWPs. This
Federal Register notice also provides a
60-day period for coastal states to
complete their CZMA consistency
determination processes. This 60-day
period will end on May 11, 2007.
While the states, Indian Tribes, and
EPA complete their WQC processes and
the states complete their CZMA
consistency determination processes,
the use of an NWP to authorize a
discharge into waters of the United
States is contingent upon obtaining
individual water quality certification or
a case-specific WQC waiver. Likewise,
the use of an NWP to authorize an
activity within, or outside, a state’s
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coastal zone that will affect land or
water uses or natural resources of that
state’s coastal zone, is contingent upon
obtaining an individual CZMA
consistency determination, or a casespecific presumption of CZMA
concurrence. We are taking this
approach to reduce the hardships on the
regulated public that would be caused
by a substantial gap in NWP coverage if
we were to wait 60 days before these
NWPs would become effective.
After the 60-day period, the latest
version of any written position take by
a state, Indian tribe, or EPA on its WQC
for any of the NWPs will be accepted as
the state’s final position on those NWPs.
If the state, Indian tribe, or EPA takes no
action by May 11, 2007, WQC will be
considered waived for those NWPs.
After the 60-day period, the latest
version of any written position take by
a state on its CZMA consistency
determination for any of the NWPs will
be accepted as the state’s final position
on those NWPs. If the state takes no
action by May 11, 2007, CZMA
concurrence will be presumed for those
NWPs.
Discussion of Public Comments
I. Overview
In response to the September 26,
2006, Federal Register notice, we
received more than 22,500 comments.
We reviewed and fully considered all
comments received in response to that
notice.
General Comments
Many commenters provided general
support for the proposal, and some of
them stated that the changes are a step
forward in improving consistency in the
NWP program. Some commenters said
that the proposed NWPs provide a
balance between environmental
protection and allowing development to
occur. One commenter said that the
NWP program provides sufficient
environmental protection, through its
general conditions and the ability for
the district engineer to exercise
discretionary authority to require
individual permits. Several commenters
stated that the proposed NWPs are
simpler, clearer, and easier to
understand. Three commenters said that
further streamlining is necessary. One
commenter recommended adopting a
standard numbering system for
paragraphs and subparagraphs within
the NWP text. Three commenters said
that the Corps should retain appropriate
references to general conditions in the
text of NWPs, for purpose of
clarification.
To the extent that it is feasible, we
have adopted a standard format for the
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NWPs. Some NWPs require different
formats, to make them easier to read and
provide further clarification. For the
most part, it is not necessary to retain
references to general conditions in the
text of the NWPs, except for general
condition 27, Pre-Construction
Notification, because most general
conditions apply to all NWPs.
In contrast, a few commenters said
that the proposed NWPs are not simpler
and clearer. Three commenters declared
that the proposed NWPs are more like
individual permits than general permits.
A number of commenters asserted that
the proposed NWPs will significantly
increase costs and delays for permit
applicants. Four commenters said that
the attempt at clarification and
simplicity will reduce the flexibility of
the NWP program.
The NWPs issued today are not
similar to individual permits. The
NWPs provide a streamlined form of
Department of the Army authorization
for those activities that result in
minimal individual and cumulative
adverse effects on the aquatic
environment and satisfy other public
interest review factors. In 2003, the
average processing time for NWPs was
27 days and for individual permits it
was 144 days. In response to comments
received as a result of the September 26,
2006, Federal Register notice, we have
modified some of the proposed NWPs to
address provisions that could have
unnecessary negative effects on
regulatory efficiency and environmental
protection.
Other commenters expressed general
opposition to the proposal, and said that
the proposal weakens protection for
waters and should be withdrawn. Many
of these commenters objected to the
goals of ‘‘streamlining’’ or ‘‘improving
regulatory efficiency,’’ stating that the
focus of the NWPs should be on
compliance with the Clean Water Act.
Some commenters expressed opposition
to the issuance of the NWPs, and said
that activities proposed for NWP
authorization should be individually
subjected to a public notice and
comment process. One commenter
suggested that pre-construction
notifications should be posted on
district web sites for at least 30 days
before an NWP verification is issued, to
allow for public comment on those
proposed activities.
The NWPs issued today comply with
the requirements of the Clean Water
Act. When the Clean Water Act was
amended in 1977, Congress recognized
the importance of general permits for
the effective and efficient
implementation of section 404. We do
not agree that pre-construction
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notifications should be posted on the
Internet for a public comment period.
The review of pre-construction
notifications by district engineers is
sufficient for effective environmental
protection. Some NWP activities require
coordination with other Federal and/or
State agencies, which provides a
supplemental level of environmental
protection. The activities authorized by
NWPs have minimal adverse effects and
are limited, within each permit, to
narrowly defined categories of similar
activities. Notice and opportunity for
public comment on the authorization of
these activities through NWPs is
provided as part of the NWP
promulgation process. The Corps
believes this is the appropriate level of
public notice and comment for these
types of activities. Further, when
reviewing pre-construction
notifications, district engineers will
exercise discretionary authority to
require individual permits for those
activities that they determine may result
in more than minimal adverse effects on
the aquatic environment or do not
satisfy other public interest review
factors, and thus warrant a more
thorough individual review through a
public notice and comment process.
Some commenters stated that the
NWPs should require consideration of
less damaging alternatives, and others
said that the Corps did not provide
sufficient scientific justification for
proposed changes to the NWPs, or
demonstrate that NWP activities result
in minimal adverse environmental
effects. One commenter said that there
is not sufficient emphasis on avoidance
of impacts to waters of the United
States. Another commenter objected to
using NWPs to expand existing projects,
stating that it discourages avoidance and
minimization.
The NWPs authorize only those
activities that result in minimal
individual and cumulative adverse
effects on the aquatic environment, and
thus do not include a formal process for
consideration of less damaging
alternatives. General condition 20,
Mitigation, requires permittees to avoid
and minimize adverse effects to the
maximum extent practicable on the
project site. The Corps believes this
ensures sufficient consideration of
alternatives for the types of low-impact
projects that are eligible for
authorization through NWPs. The Corps
notes that expansion of existing projects
may support the goals of avoidance and
minimization, in contrast to the
alternative of developing new sites,
which may involve more substantial
adverse impacts. The 404(b)(1)
Guidelines contain flexibility for those
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activities that result in minimal adverse
effects on the aquatic environment.
Compliance with the National
Environmental Policy Act and the
Section 404(b)(1) Guidelines is
accomplished through decision
documents prepared by the Corps.
These decision documents contain
findings that the NWPs result in
minimal adverse effects, and are based
on available data at the national scale.
Division engineers issue supplemental
decision documents for use of NWPs
within Corps district boundaries.
Several commenters said that the
NWPs do not protect small wetlands
and waterbodies enough, and one
commenter said that the proposed
permits do not support the ‘‘no overall
net loss’’ goal for wetlands. In contrast,
one commenter stated that the proposal
provides adequate protection to the
environment and supports the ‘‘no
overall net loss’’ of wetlands goal.
The NWPs protect all jurisdictional
waters, including small wetlands and
other waterbodies, through their terms
and conditions, such as acreage limits
and linear foot limits. The NWPs also
support the ‘‘no overall net loss goal’’
through mitigation requirements,
including aquatic resource restoration,
establishment, enhancement, and
preservation activities that may be
required as compensatory mitigation. As
noted above, general condition 20,
Mitigation, also includes requirements
for on-site avoidance and minimization.
Two commenters objected to allowing
district engineers to issue waivers that
allow permittees to exceed the limits of
NWPs, stating that such waivers do not
support the minimal adverse effects
requirement. Two commenters said that
the NWPs authorize unlimited impacts
to waters of the United States. One
commenter remarked that acreage limits
should be consistent for all NWPs. One
commenter stated that the acreage limits
in the proposed NWPs are sufficient to
ensure minimal adverse effects. Three
commenters asserted that the acreage
limits of the proposed NWPs are too
low, and they reduce the effectiveness
of the NWP program. One commenter
said that the low acreage limits for the
NWPs lessen incentives to reduce
impacts to waters, since many projects
that previously qualified for NWP
authorization now require individual
permits. Another commenter stated that
the acreage limits for all NWPs should
be based on appropriate scientific and
environmental criteria.
Many of the NWPs have acreage
limits, and most of those that do not are
self-limiting due to the nature of the
authorized activity (e.g., NWP 1 for aids
to navigation or NWP 10 for mooring
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buoys). Acreage limits in NWPs cannot
be waived by the district engineer.
Linear foot limits in some permits can
be waived, but only for intermittent and
ephemeral (not perennial) streams. Two
NWPs (i.e., NWPs 13 and 36) have cubic
yard limits that may be waived. Those
NWPs that contain provisions allowing
district engineers to waive linear foot or
cubic yard limits require the district
engineer to make a written
determination of minimal adverse
effects. In such cases, the permittee
cannot assume that a waiver was
granted if the district engineer does not
affirm that waiver in writing (see
general condition 27). The Corps
believes these limited waiver provisions
are appropriate because activities that
exceed the limits may still have
minimal adverse impacts and it may
require a site-specific evaluation by the
district engineer to decide if they do.
Other NWPs that do not have limits
typically provide environmental
benefits, such as aquatic resource
restoration activities authorized by NWP
27 or hazardous and toxic waste
cleanup activities authorized by NWP
38.
NWPs 21, 49, and 50 are a special
case, in that they authorize activities for
which review of environmental impacts,
including impacts to aquatic resources,
is separately required under other
Federal authorities (e.g., Surface Mining
Control and Reclamation Act (SMCRA)
permits for coal mining activities). The
Corps believes it would be
unnecessarily duplicative to separately
require the same substantive analyses
through an individual permit
application as are already required
under SMCRA. However, through the
pre-construction notification review
process, the district engineer will
consider the analyses prepared for the
SMCRA permit and exercise
discretionary authority to require an
individual permit in cases where the
district engineer determines, after
considering avoidance and reclamation
activities undertaken pursuant to
SMCRA, that the residual adverse
effects are not minimal. The project
sponsor is required to obtain written
verification prior to commencing work.
The acreage limits for the NWPs are
established so that they authorize most
activities that result in minimal adverse
effects on the aquatic environment. We
acknowledge that there may be some
activities that exceed the acreage limits
and still have minimal impacts but the
Clean Water Act requires us to ensure
that all projects authorized by NWPs
have minimal impacts, not that all
minimal-impact projects can be
authorized by NWPs. Activities that are
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not authorized through NWPs may be
authorized through regional general
permits or individual permits.
One commenter stressed that the
NWPs must be reissued in time, so that
there is no gap between the expiration
date of the current NWPs and the
effective date of the new NWPs. Two
commenters recommended
administratively extending the current
NWPs until the effective date of the new
NWPs, through 5 U.S.C. 558(c), which is
used to administratively extend
National Pollutant Discharge
Elimination System (NDPES) permits
issued under Section 402 of the Clean
Water Act.
We cannot use 5 U.S.C. 558(c) to
administratively extend the NWPs,
since that provision of the
Administrative Procedures Act applies
only to activities of ‘‘a continuing
nature’’ such as discharges of effluents
authorized by National Pollutant
Discharge Elimination System permits
issued under Section 402 of the Clean
Water Act. The vast majority of
activities authorized by NWPs are
construction activities, with specific
start and end dates, either for the
discharge of dredged or fill material into
waters of the United States, or structures
or work in navigable waters of the
United States. In general, these NWP
activities are not of a continuing nature,
and do not meet the requirements of 5
U.S.C. 558(c). The grandfather provision
at 33 CFR 330.6(b) can be used to
continue the authorization for those
NWP activities that are under
construction, or under contract to begin
construction, after the NWP expires.
This provision of the NWP regulations
allows the permittee up to one year to
complete the authorized NWP activity.
Today’s reissued and new permits will
become effective on March 19, 2007, the
day after the existing permits expire.
Thus there will be no gap in coverage.
The Corps expects that some States may
be able to make their final Section 401
water quality certifications for all or
some permits by this date. In cases
where the State has not completed a 401
water quality certification by this time,
the Corps will issue provisional
verifications and permittees will be
required to obtain individual State
certifications prior to commencing
discharges into waters of the United
States.
Compliance With Section 404(e) of the
Clean Water Act and the 404(b)(1)
Guidelines
Several commenters said that the
proposed NWPs are contrary to the
intent of section 404(e) to provide an
expedited, streamlined permit program
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for activities that have minimal
environmental impacts.
The NWPs continue to provide a
streamlined authorization process for
those activities that result in minimal
individual and cumulative adverse
effects on the aquatic environment.
Those activities that do not qualify for
NWP authorization may be authorized
by regional general permits or
individual permits.
Many commenters asserted that the
NWPs result in more than minimal
adverse effects on the aquatic
environment, individually and
cumulatively. Several commenters said
that the NWPs do not comply with the
404(b)(1) Guidelines. One commenter
said that the Corps should provide
quantitative statistics on actual impacts,
to predict cumulative impacts resulting
from the NWPs. Two commenters
believe that the draft decision
documents do not adequately
demonstrate that NWPs will result in
minimal individual and cumulative
impacts to waters of the United States.
They said that there is not sufficient
documentation to support estimates of
the number of times an NWP will be
used, the acres impacted, and the acres
mitigated. They also stated that there
should be more specific evaluations of
particular types of waters, as well as
landscape considerations. Four
commenters said that the Corps cannot
rely on mitigation to ensure minimal
adverse effects, stating that the
evaluation of minimal adverse effects
must be completed prior to issuing a
general permit. Therefore, the Corps
cannot rely on mitigation that will be
offered by permittees when making its
finding under the 404(b)(1) Guidelines.
When we issue the NWPs, we fully
comply with the requirements of the
404(b)(1) Guidelines at 40 CFR 230.7,
which govern the issuance of general
permits under section 404. For the
section 404 NWPs, each decision
document contains a 404(b)(1)
Guidelines analysis. Section 230.7(b) of
the 404(b)(1) Guidelines requires only a
‘‘written evaluation of the potential
individual and cumulative impacts of
the categories of activities to be
regulated under the general permit.’’
Since the required evaluation must be
completed before the NWP is issued, the
analysis is predictive in nature. The
estimates of potential individual and
cumulative impacts, as well as the
projected compensatory mitigation that
will be required, are based on the best
available data from the Corps district
offices, based on past use of NWPs. In
our decision documents, we also used
readily available national data on the
status of wetlands and other aquatic
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habitats in the United States, and the
potential impacts of the NWPs on those
waters.
The 404(b)(1) Guidelines at 40 CFR
230.7 do not prohibit the consideration
of mitigation when making the
predictive evaluation of potential
individual and cumulative impacts that
may be authorized by an NWP. The
practice of using compensatory
mitigation to ensure minimal adverse
individual and cumulative adverse
effects is an important component of the
NWP program (see 33 CFR 330.1(e)(3)).
Two commenters said that the Corps
cannot rely on regional conditioning
and discretionary authority to ensure
minimal adverse effects. One
commenter objected to the ability of the
district engineer to exercise
discretionary authority to impose
conditions on NWP activities. Another
commenter stated that in order to ensure
minimal adverse effects, preconstruction notification should be
required for all NWPs. A number of
commenters said that many of the NWPs
do not authorize activities that are
similar in nature. They said that the
Corps is required to explain why
activities authorized by an NWP are
similar in nature to warrant
authorization under a single NWP.
The pre-construction notification
review process and discretionary
authority are important tools to help
ensure that the NWPs authorize only
those activities with minimal individual
and cumulative adverse effects. If the
district engineer reviews a preconstruction notification and
determines that the impacts are more
than minimal, discretionary authority
will be exercised and either the NWP
will be conditioned to require
mitigation or other actions to ensure
minimal adverse effects or an individual
permit will be required. The Corps
disagrees that pre-construction
notification is necessary for all NWP
activities. However, the Corps has
expanded the scope of activities
requiring pre-construction notification.
Specifically, all activities conducted
under NWPs 7, 8, 17, 21, 29, 31, 33, 34,
37, 38, 39, 40, 42, 44, 45, 46, 49, and 50
now require pre-construction
notification, regardless of acreage
impacted. This will enable district
engineers to better ensure that these
permits authorize only activities with
minimal impacts.
These NWPs satisfy the requirement
under Section 404(e) of the Clean Water
Act that the categories of authorized
activities be similar in nature. The
‘‘similar in nature’’ provision does not
require NWP activities to be identical to
each other. We believe that the
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‘‘categories of activities that are similar
in nature’’ requirement of section 404(e)
is to be interpreted broadly, for practical
implementation of this general permit
program. Nationwide permits, as well as
other general permits, are intended to
reduce administrative burdens on the
Corps and the regulated public, by
efficiently authorizing activities that
have minimal adverse environmental
effects. For each NWP that authorizes
activities under Section 404 of the Clean
Water Act, the 404(b)(1) Guidelines
analysis provides a brief explanation as
to why the activities authorized by that
NWP are similar in nature.
One commenter said that
consideration of impacts resulting from
general permits should not be limited to
the aquatic environment. This
commenter said that Section 404(e) of
the Clean Water Act requires permitted
activities to have minimal impacts on
the environment as a whole.
In addition to the requirement that
there be no more than minimal adverse
effects on the aquatic environment,
activities authorized by NWPs must also
result in minimal adverse effects with
regards to the Corps public interest
factors (see 33 CFR 330.1(d)), which
include other components of the
environment.
Compliance With the National
Environmental Policy Act
Many commenters said that the Corps
must complete an Environmental
Impact Statement for the proposed
NWPs. One commenter remarked that
the EIS must consider the individual
impacts of the NWPs, as well as their
cumulative impacts. One comment
asserted that mitigation cannot be used
to justify using an environmental
assessment for NEPA compliance,
instead of an Environmental Impact
Statement.
The NWPs authorize activities that
have minimal individual and
cumulative adverse effects on the
aquatic environment and satisfy other
public interest review factors. The
NWPs do not reach the level of
significance required for an EIS. The
Corps complies with the requirements
of the NEPA by preparing an
environmental assessment for each
NWP. When an NWP is issued, a
Finding of No Significant Impact is also
issued.
The use of mitigation to make a
Finding of No Significant Impact is a
standard practice for NEPA compliance.
For the purposes of NEPA, mitigation
includes avoiding impacts, minimizing
impacts, rectifying impacts through
repairing or restoring the affected
environment, reducing or eliminating
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impacts over time through preservation
and maintenance activities, and
compensating for impacts by replacing
or providing resources or environments
(see 40 CFR 1508.20). Through the
requirements of general condition 20,
Mitigation, the review of preconstruction notifications by district
engineers, and regional and special
conditions imposed on the NWPs by
division and district engineers, NWP
activities use all these forms of
mitigation so that the adverse effects of
the NWPs do not reach the level of
significance that requires an
Environmental Impact Statement.
Several commenters stated that the
draft decision documents do not satisfy
the requirements of the National
Environmental Policy Act (NEPA).
Some commenters said that the analyses
in the decision documents are not based
on realistic data. One commenter noted
that the average impact is often much
less than the acreage limit for the NWP,
and said that the mitigation ratios seem
too high. One commenter said that the
environmental assessments in draft
decision documents must contain sitespecific analyses. Two commenters
asserted that the cumulative effects
analyses in the decision documents are
inadequate. One commenter said that
the cumulative effects analysis should
include information on the past use of
NWPs, as well as information on other
development activities expected to have
impacts on protected resources.
We believe the data in the draft
decision documents comply with the
requirements of NEPA. The estimates of
the projected use of the NWPs, the acres
impacted, and the amount of
compensatory mitigation are based on
available data from Corps district
offices, and other sources of data, such
as surveys. Those data are based on preconstruction notifications and other
requests for NWP verifications for
activities that do not require preconstruction notification. For those
NWP activities that do not require
notification, it is necessary to derive
estimates. For the decision documents,
we must use predictive data, since the
future use of an NWP is speculative.
Likewise, we cannot provide sitespecific information for these
environmental assessments, because
there are no specific sites or projects
associated with the proposed issuance
of an NWP. Authorized impacts are
usually much less than the acreage limit
for an NWP because of the avoidance
and minimization required by the terms
and conditions of the NWPs. The
compensatory mitigation data provided
in the decision documents include
preservation.
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On June 24, 2005, the Council on
Environmental Quality issued guidance
on the consideration of past actions for
cumulative effects analyses. According
to this guidance, the cumulative effects
analysis needs to consider relevant past
actions that can be used to analyze
reasonably foreseeable effects that have
‘‘a continuing, additive, and significant
relationship to those effects.’’ The
guidance also recommends that agencies
look at the present effects of past actions
that are relevant because of significant
cause-and-effect relationships with the
effects for the proposed action and its
alternatives. Except for a few activities,
the NWPs do not authorize activities of
a continuing nature. In general, they
authorize construction activities with
specific start and end dates. The NWPs
can be issued for only a period of five
years or less, and once an NWP expires,
it cannot be used to authorize activities
in waters of the United States. An
activity must then be authorized by the
reissued NWP, another NWP, a regional
general permit, or an individual permit.
The cumulative effects analysis is more
properly focused on the permits that can
be used to authorize regulated activities,
not past permits that have expired.
Therefore, the cumulative effects
analysis for the NWP issuance needs to
focus on the reasonably foreseeable
cumulative effects that are expected to
occur during the five year period the
NWPs are valid. We use information on
past use of the NWPs to estimate how
often an NWP will be used during the
period it will be valid, and to estimate
the impacts and compensatory
mitigation resulting from the use of that
NWP.
One commenter requested
clarification as to whether the draft
decision documents included an
environmental assessment, an EIS, or
another type of NEPA document. Two
commenters remarked that the Corps
failed to solicit public comment on the
environmental assessments for the
proposed NWPs. Two commenters
objected to the Finding of No Significant
Impact (FONSI) in each draft decision
document, stating that it is
inappropriate to do a FONSI for a
proposed action. Another commenter
concurred with the FONSI found in
each NWP decision document. One
commenter said that the draft decision
documents accurately analyzed
anticipated environmental effects of the
proposed NWPs.
A draft environmental assessment was
prepared for each of the proposed
NWPs. The draft environmental
assessment was in the draft decision
document, along with the draft
statement of findings and, if the NWP
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authorized activities under Section 404
of the Clean Water Act, a draft Section
404(b)(1) Guidelines analysis. Those
draft decision documents were available
for public review and comment at the
same time as the proposed NWPs,
general conditions, and definitions. A
number of commenters who commented
on the proposed NWPs also commented
on the draft decision documents.
Commenters could also provide input
on the draft FONSI in each decision
document.
Compliance With the Endangered
Species Act
In the September 26, 2006, Federal
Register notice, we stated that we will
conduct Endangered Species Act
Section 7(a)(2) consultation for the
NWPs. Since the issuance of the
September 26, 2006, proposal, the Corps
has been working with the National
Marine Fisheries Service (NMFS) and
the U.S. Fish and Wildlife Service
(USFWS) to develop an analysis plan to
guide the formal programmatic Section
7 consultation for the NWPs. As soon as
the analysis plan is completed, the
Corps will request programmatic
Endangered Species Act Section 7(a)(2)
consultation with the USFWS and
NMFS. Prior to the effective date of
these NWPs, the Corps will issue a
section 7(d) determination for the NWP
Program.
Two commenters said the Corps must
conduct Endangered Species Act
consultation before the NWPs are
issued. One of these commenters said
that the Corps must conduct
programmatic section 7 consultation for
the NWP program, with mandatory
district-by-district formal consultations.
One commenter requested a timeline for
the programmatic Section 7 consultation
with the USFWS and NMFS. Another
commenter asked for clarification
whether Section 7 ESA consultation
will be conducted for each NWP
authorization or the NWP program as a
whole. One commenter objected to the
Corps conducting section 7 consultation
for coal mining activities authorized by
the Surface Mining Control and
Reclamation Act.
The programmatic ESA consultation
will be conducted for the NWP program
as a whole, and will be concluded as
expeditiously as possible. To address
ESA compliance while programmatic
consultation is being conducted, a
revised Section 7(d) determination will
be issued for the NWP program before
the effective date of these NWPs. The
Section 7(d) determination discusses
how the issuance of these NWPs will
not foreclose any options. The
requirements of general condition 17
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and 33 CFR 330.4(f) will ensure
compliance with the ESA. We anticipate
that the programmatic consultation will
result in a biological opinion that
provides tools that districts can use to
better address potential impacts to the
endangered and threatened species that
occur in their areas of regulatory
jurisdiction. Corps districts will conduct
their own formal Section 7
consultations as necessary. The
programmatic consultation will be
conducted for the NWP program; its
applicability to NWP 21 and other
NWPs will be addressed as part of the
programmatic consultation itself.
One commenter said that the Corps
cannot rely on permit applicants to
notify them in cases where ESA
consultation is necessary. Two
commenters said that the proposed
changes to general condition 17, which
requires district engineers to notify
prospective permittees of their ‘‘no
effect’’ or ‘‘may affect’’ determinations
within 45 days of receipt of a complete
pre-construction notification, violates
the ESA since the Corps will be unable
to make its decision based on the best
available science. Two commenters said
that the Corps must require preconstruction notifications for all NWP
activities to help ensure compliance
with the requirements of the ESA. Two
other commenters stated that speciesspecific regional conditions must be
imposed on the NWPs to protect
endangered and threatened species.
Non-federal permittees shall notify
the district engineer if any listed species
or designated critical habitat might be
affected or is in the vicinity of the
project, or if the project is located in
designated critical habitat, and in such
cases shall not begin work on the
activity until notified by the district
engineer that the requirements of the
ESA have been satisfied and that the
activity is authorized. This requirement
applies even when a pre-construction
notification would not otherwise be
required. In such cases, this condition
also prohibits the prospective permittee
from conducting the NWP activity until
the district engineer notifies him or her
that the requirements of the ESA have
been fulfilled and the activity is
authorized by NWP. The ESA
regulations at 50 CFR part 402 do not
require ESA consultation for those
activities that will not affect endangered
or threatened species or destroy or
modify designated critical habitat. In
some districts, regional conditions will
be imposed on the NWPs to protect
listed species and critical habitat.
The notification requirement in
general condition 17 does not violate
the ESA. Forty-five days is generally
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sufficient to screen proposed activities
for potential effects to endangered and
threatened species or designated critical
habitat, and determine if section 7
consultation is necessary. The
notification requirement will help
improve ESA compliance by keeping
the prospective permittee aware of the
status of his or her pre-construction
notification and preclude applicants
from assuming that they can proceed
after the 45 day pre-construction
notification period has ended, if they
have not heard back from the Corps that
ESA requirements have been fulfilled
and the activity is authorized. Districts
will continue to develop regional
conditions to further protect endangered
and threatened species, as well as
critical habitat.
Linear Foot Limits for Stream Bed
Impacts
In the September 26, 2006, Federal
Register notice, we proposed to modify
several NWPs to include ephemeral
streams in the 300 linear foot limits for
losses of stream beds. We also proposed
to allow district engineers to issue
written waivers to the 300 linear foot
limit for intermittent and ephemeral
streams, upon making a determination
that the adverse effects on the aquatic
environment will be minimal. Many
commenters objected to including
ephemeral streams in the 300 linear foot
limit for stream beds for NWPs 29, 39,
40, 42, and 43. Many other commenters
supported the proposed change. A large
number of commenters objected to
allowing district engineers to waive the
300 linear foot limit, stating that miles
of stream bed could be lost, resulting in
more than minimal adverse
environmental effects. A few
commenters supported the proposed
waiver. One commenter said that limits
to filling or excavating ephemeral
streams should be addressed through
the regional conditioning process,
instead of the national terms and
conditions of the NWPs. Another
commenter recommended imposing a
higher linear foot limit for losses of
ephemeral streams.
Ephemeral streams are important
components of the stream network.
Applying the 300 linear foot limit to
ephemeral stream beds will help ensure
that the applicable NWPs will authorize
activities with minimal individual and
cumulative adverse effects on the
aquatic environment. The ability of
district engineers to issue written
waivers of the 300 linear foot limit for
intermittent and ephemeral stream beds
provides flexibility in the
administration of the NWP program. In
cases where the 300 linear foot limit is
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waived, the acreage limit of the NWP
still applies. We believe it is more
appropriate to limit losses of ephemeral
stream beds through the national NWP
terms and conditions, to provide
consistent protection for those waters
across the country. Regional differences
in the values applied to ephemeral
stream functions and services can be
addressed through the waiver process.
We believe the 300 linear foot limit, in
conjunction with the waiver process,
provides sufficient flexibility for the
NWP program while ensuring minimal
adverse effects.
Three commenters recommended that
the Corps modify its definition of
‘‘ephemeral stream’’ to simplify the
process of distinguishing between
ephemeral and intermittent streams
instead of applying the 300 linear foot
limit to ephemeral streams. Another
commenter indicated that the difficulty
of distinguishing between ephemeral
and intermittent streams is sufficient
justification for including ephemeral
streams in the 300 linear foot limit. In
contrast, several commenters stated that
including ephemeral streams in the 300
linear foot limit would not simplify the
administration of the NWP program,
because it would result in a large
number of individual permits, as well as
substantial increases in the Corps
workload. Two commenters asked the
Corps to establish criteria for
determining when a waiver of the 300
linear foot limit can be issued. One
commenter stated that the 300 linear
foot limit should not apply to filling or
excavating drainage ditches. One of
these commenters said that an acreage
limit should be applied to streams,
instead of a linear foot limit.
Modifying the definition of
‘‘ephemeral stream’’ is not an
appropriate alternative to modifying the
300 linear foot limit. The definitions of
‘‘ephemeral stream’’ and ‘‘intermittent
stream’’ that were first promulgated for
the NWPs in 2000 are based on the
hydrologic differences between those
stream types, especially the differences
in how the stream bed interacts with the
water table. We do not agree that the
changes to the 300 linear foot limit will
result in a large increase in the number
of individual permits processed per
year. Under the current NWPs, district
engineers could exercise discretionary
authority and require individual permits
if proposed impacts to ephemeral
streams would be more than minimal.
We do not believe it would be
appropriate to establish national criteria
for determining when a waiver of the
300 linear foot limit would be applied.
These determinations should be made
on a case-by-case basis by district
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engineers, depending upon assessments
of site-specific conditions. Even though
the acreage limits of NWPs 29, 39, 40,
42, and 43 also apply to losses of stream
bed, the linear foot limit is a useful tool
for ensuring minimal adverse effects to
these linear aquatic ecosystems. The 300
linear foot limit for filling and
excavating stream beds does not apply
to ditches constructed in wetlands, or to
ditches constructed in uplands that are
determined to be waters of the United
States. However, the 300 linear foot
limit does apply to ditches that are
constructed by modifying streams
through channelization or other
activities.
Pre-Construction Notification
Many commenters objected to the
proposal to add or expand preconstruction notification requirements
for several NWPs, and a few of these
commenters said that lowering the preconstruction notification threshold will
substantially increase the Corps
workload. Several commenters stated
that increasing the number of activities
that require pre-construction
notification will result in additional
delays and costs for permit applicants.
In contrast, a number of commenters
said that pre-construction notification
should be required for all NWP
activities, so that site-specific concerns
can be more effectively addressed. One
commenter asserted that the use of the
pre-construction notification process
and the use of discretionary authority
should be limited, to provide more
certainty to the NWP authorization
process. Another commenter said that
the decision to lower pre-construction
notification thresholds should be left to
division engineers and the regional
conditioning process, to provide more
flexibility for the NWP program.
Modifying NWPs 39, 40, 42, and 43 to
require pre-construction notification for
all activities will help ensure that these
NWPs authorize only those activities
that result in minimal individual and
cumulative adverse effects on the
aquatic environment and other public
interest review factors, such as flood
hazards and floodplain values. Corps
districts have already been receiving
large numbers of verification requests
for NWP 39, 40, 42, and 43 activities
that do not require pre-construction
notification, so we believe that this
change will not result in a substantial
increase in our workload. In addition,
the modified pre-construction
notification threshold will facilitate
compliance with the Endangered
Species Act and Section 106 of the
National Historic Preservation Act, by
better ensuring notice of activities that
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may have a higher likelihood of
affecting endangered or threatened
species, designated critical habitat, or
historic properties. We do not agree that
it is necessary to require preconstruction notifications for all NWP
activities, because many NWP activities
have negligible effects on the aquatic
environment and the public interest
review factors. We have focused the preconstruction notification requirements
on those activities that have the
potential for adverse effects that may
require additional scrutiny by district
engineers, including ESA and/or NHPA
consultation.
The pre-construction notification and
discretionary authority processes
provide flexibility to the Corps
regulatory program, by allowing the
Corps to focus its limited resources on
activities that have the potential to have
more than minimal adverse effects on
the aquatic environment. We believe
that the proposed changes to the preconstruction notification thresholds are
necessary for effective implementation
of the NWP program, and to address
issues of concern at the national level.
One commenter objected to the
increased use of the pre-construction
notification process and the waivers of
limits, such as the 300 linear foot limit
for the loss of intermittent and
ephemeral stream beds for certain
NWPs, to authorize activities by NWP.
Another commenter said that it is an
administrative burden to require the use
of NWP 33 with other NWPs when instream construction activities need to
occur in dry conditions. This
commenter said that NWP 33 should
only be used when temporary work is
done in waters of the United States, and
no other NWP is needed to authorize
permanent structures or fills for the
activity. One commenter recommended
requiring pre-construction notifications
for filling waters of the United States
that are five or more feet deep, because
of the effects on the hydrologic balance
of a region.
The ability to waive limits after the
review of a pre-construction notification
and a written determination that the
adverse effects of a particular NWP
activity will be minimal provides
flexibility to the NWP program, and
allows the Corps to focus more of its
resources on those activities that require
individual permits and may have
substantial adverse effects on the
aquatic environment and the public
interest. In the final NWPs, we have
addressed the concern regarding the
requirement to use NWP 33 for all
temporary construction, access, and
dewatering activities. Those changes are
discussed in further detail for each
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applicable NWP. Many NWP activities
that result in a discharge of dredged or
fill material into waters of the United
States, regardless of water depth, require
pre-construction notification, which
will allow district engineers to review
those activities on a case-by-case basis
and assess potential effects on the
hydrologic balance of the area in the
vicinity of the proposed work.
One commenter said that the preconstruction notification process should
be modified to require notification of
Indian Tribes, to provide them with the
opportunity to comment on proposed
activities that may result in the violation
of Indian rights. This commenter also
said that if the Indian Tribe identifies a
potential conflict with Federallyprotected Indian rights, the use of the
NWPs should not be allowed.
The regional conditioning process, as
well as government-to-government
consultation between Tribes and the
Corps districts where Tribal lands are
located, are more appropriate
mechanisms to address this
commenter’s concerns, since there are
over 580 Federally-recognized tribes,
and each Tribe is likely to have different
concerns regarding the implementation
of the NWP program. General condition
16 states that no NWP activity may
impair reserved Tribal rights. Activities
that do impair reserved Tribal rights are
not authorized by NWPs. Regional
conditions are an effective mechanism
for addressing the concerns of a specific
Indian Tribe, and can be used to
facilitate working relationships between
the Corps and the Tribe to help the
Corps fulfill its trust responsibilities.
Clean Water Act Jurisdiction
On June 19, 2006, the Supreme Court
issued its decision in the case of
Rapanos et ux, et al, v. United States.
Many commenters cited this decision,
as well as other court decisions, and
said that the proposed NWPs exceed the
Corps jurisdictional authority under
Section 404 of the Clean Water Act.
Several commenters said that ephemeral
streams are not subject to Clean Water
Act jurisdiction and should not be
covered in the NWPs. Another
commenter asserted that intermittent
streams are not waters of the United
States.
The Rapanos decision, as well as
other court decisions made in the past
several years, raises questions about the
jurisdiction of the Clean Water Act,
including Section 404, over some
intermittent and ephemeral streams and
their adjacent wetlands. The Corps will
assess jurisdiction regarding such
waters on a case-by-case basis in
accordance with evolving case law and
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any future guidance that may be issued
by appropriate Executive Branch
agencies (e.g., the Corps, U.S.
Environmental Protection Agency).
Under the current regulations and
guidance, intermittent and ephemeral
streams may meet the regulatory
definition of ‘‘waters of the United
States’’ and be subject to Clean Water
Act jurisdiction. Regulatory jurisdiction
over these waterbodies will be
determined on a case-by-case basis by
district engineers, in accordance with
current and future regulations and
guidance.
One commenter said that when
applying the NWP acreage limits to
wetlands, the Corps should not include
all wetlands, just those subject to Clean
Water Act jurisdiction. One commenter
stated that a clearer definition of
‘‘navigable waters’’ is needed. Another
commenter said that ditches are not
waters of the United States, and impacts
to ditches should instead be addressed
through state programs. A commenter
stated that the Corps must promulgate
regulations to define ‘‘waters of the
United States’’ for the purposes of
implementing the NWP program.
The acreage limits of the NWPs apply
only to losses of waters of the United
States, including jurisdictional wetlands
(see the definition of the term ‘‘loss of
waters of the United States’’ in the
‘‘Definitions’’ section of the NWPs).
Similarly, linear foot limits apply only
to jurisdictional streams. Ditches may
also be subject to jurisdiction under
Section 404 of the Clean Water Act and/
or Section 10 of the Rivers and Harbors
Act of 1899, if they meet the regulatory
definitions of ‘‘waters of the United
States’’ and/or ‘‘navigable waters of the
United States.’’ Waters of the United
States are defined at 33 CFR part 328
and navigable waters of the United
States are defined at 33 CFR part 329.
Regional Conditioning of Nationwide
Permits
One commenter stated that regional
conditions are unnecessary, and result
in too much restriction of the NWPs. A
commenter remarked that placing too
many regional conditions on the NWPs
is contrary to E.O. 13274,
Environmental Stewardship and
Transportation Infrastructure Project
Reviews. One commenter said that
regional conditions should not be
redundant with the requirements of
other agencies, and the streamlining
objective of the NWPs should be
maintained.
Regional conditions are necessary to
account for regional differences in
aquatic resource functions, services, and
values and to ensure that the NWPs
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authorize only those activities that have
minimal individual and cumulative
adverse effects on the aquatic
environment and other public interest
review factors. Regional conditions are
important tools for protecting
endangered and threatened species,
designated critical habitat for those
species, essential fish habitat, historic
properties, and other important
resources. As a general matter, we agree
that regional conditions should not
duplicate the requirements of other
agencies, but the Corps often has the
responsibility to comply with other
statutes and regulations administered by
other agencies.
Two commenters said that there
needs to be clearer rules for the
adoption of regional conditions for the
NWPs. A couple of commenters
indicated that districts need to provide
justifications for proposed regional
condition, and make that information
available to the public. Three
commenters said that regional
conditions should not be limited to
further restricting the use of the NWPs.
One commenter said that regional
conditions should not be based on
district boundaries. Instead, they should
be based on ecoregions or other
ecologically-delineated areas. Another
commenter recommended that the
Corps work with other agencies to
develop a list of high value wetlands in
which NWPs cannot be used.
Regional conditions may only further
condition or restrict the applicability of
an NWP (see 33 CFR 330.1(d)). In areas
where environmental conditions and
other circumstances warrant less
restrictive general permit conditions,
district engineers may issue regional
general permits to authorize similar
activities, as long as those general
permits meet applicable requirements.
The regulations governing the adoption
of regional conditions are provided at 33
CFR 330.5(c). We believe it is necessary
to provide flexibility to division
engineers to determine the necessity
and appropriateness of regional
conditions to address concerns
regarding the use of NWPs in a
particular area. The notices issued by
Corps districts soliciting public
comment on proposed regional
conditions are required to include
statements concerning the
environmental factors or other public
interest factors resulting in the need for
regional conditions (see 33 CFR
330.5(c)(1)). Regional conditions may be
based on geographic areas other than
district boundaries. Regional conditions
may be imposed on the use of NWPs in
watersheds, counties, states, ecoregions,
or other types of areas. General
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condition 19, designated critical
resource waters, provides a national list
of high value waters. Districts can
coordinate with other agencies to
develop lists of high value wetlands
within their district boundaries.
Data Collection
One commenter said that the
supporting data used by the Corps falls
short of the standards required by the
Data Quality Act of 2001, and the Office
of Management and Budget’s
‘‘Guidelines for Ensuring and
Maximizing the Quality, Objectivity,
Utility, and Integrity of Information
Disseminated by Federal Agencies.’’
This commenter stated that the Corps
should provide data on aquatic resource
functions to support its minimal impact
determinations.
The data used for the NWP decision
documents are the best available data at
a national scale. The estimated impacts
and mitigation provided in the decision
documents were developed by
reviewing and analyzing permit data
from our district offices, as well as
through consideration of how proposed
changes to the NWPs would affect the
amounts of authorized impacts and
mitigation. Data on aquatic resource
functions is generally not available. The
National Wetland Inventory examines
wetland status and trends for the
conterminous United States, but
information on wetland quality and
function is not available.
Three commenters expressed concern
about tracking permanent and
temporary impacts to waters of the
United States and recommended that
the Corps implement a national tracking
and monitoring system. This system
would also facilitate the sharing of
information with cooperating resource
agencies and help improve decision
making.
We are in the process of transitioning
to a new automated information system
(AIS) for the Corps regulatory program.
The new AIS is version 2.0 of the
‘‘OMBIL Regulatory Module’’ (ORM
2.0). This national tracking and
monitoring system will improve and
standardize data collection for the Corps
regulatory program, and will assist in
decision-making for permit actions and
other types of regulatory activities, such
as jurisdictional determinations. ORM
2.0 will be spatially enabled, using
geographic information systems and
other analytical tools that will provide
more efficient and effective processing
of permit applications, jurisdictional
determinations, and other tasks.
Cumulative impact analysis will also be
supported by ORM 2.0. The structure of
ORM 2.0 will also be standard among
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Corps districts, providing for more
consistent information collection and
storage, and will be readily available for
analysis and reporting. The standard
structure of ORM will also promote
consistency in Regulatory Program
implementation.
ORM 2.0 will help improve data
collection for the NWP program, as well
as other types of permits issued by the
Corps. Data collection will be more
standard among permit types, especially
for impact and mitigation data. We will
continue to collect data on authorized
losses of waters of the United States,
including resource type, acreage, and
impact type. ORM 2.0 incorporates
several additional AIS resources to
assist in the tracking of all required
compensatory mitigation, including the
amount, type (e.g., reestablishment), and
source (i.e., permittee-responsible
mitigation, mitigation bank, or in-lieu
fee).
ORM 2.0 will also facilitate
compliance with the Endangered
Species Act, the National Historic
Preservation Act, and the essential fish
habitat provisions of the MagnusonStevens Fishery Management and
Conservation Act. Screening tools based
on available data for those resources
will help Corps personnel identify
activities that may affect those resources
and require further consultation. The
available resource data will be provided
by other agencies, through data sharing
agreements. Available data sets from the
national, state, and local levels can be
utilized by ORM 2.0.
ORM 2.0 is capable of supporting
electronic interagency coordination. For
activities that typically require
interagency coordination and
consultation, agencies will have the
option of receiving electronic
coordination notices and consultation
requests and of responding to the Corps
via a link to ORM 2.0. Agencies will be
required to enter into a Memorandum of
Agreement supporting the use of
electronic communications for permit
activities.
ORM 2.0 will also include time
tracking features to help remind Corps
project managers when the end of the
45-day pre-construction notification
review will occur. Monitoring and
enforcement activities will also be
supported by ORM 2.0, including the
tracking of when monitoring reports for
compensatory mitigation projects are
due.
ORM 2.0 will also support an
electronic permit application, thereby
allowing prospective permittees to
submit their pre-construction
notifications electronically to the
appropriate Corps district. Permit
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applicants will be able to check the
status of their permit applications
through the electronic permit Web site.
Other Issues
One commenter said that the Corps
should stop issuing NWPs until
effective compensatory mitigation is
provided for those permits. Several
commenters stated that the Corps places
too much reliance on compensatory
mitigation, citing recent studies that
concluded that compensatory mitigation
projects often fail to achieve their
objectives. A couple of commenters
asserted that the Corps should not rely
on compensatory mitigation to ensure
minimal individual and cumulative
adverse effects. Another commenter
objected to the more stringent
requirements for compensatory
mitigation for NWP activities, stating
that compensatory mitigation for small
impacts tends to be more expensive
than the costs to plan and construct the
proposed activity requiring NWP
authorization.
Compensatory mitigation is an
important mechanism to help ensure
that the NWPs authorize activities that
result in minimal individual and
cumulative adverse effects on the
aquatic environmental. We acknowledge
that the ecological success of
compensatory mitigation projects varies
widely. Some compensatory mitigation
projects fail to meet their objectives,
while others do result in successful
replacement of aquatic resource
functions that are lost as a result of
activities authorized by NWPs. We are
committed to improving compliance for
compensatory mitigation required for
Department of the Army permits,
including NWPs. District engineers have
the flexibility to determine when
compensatory mitigation should be
required for activities authorized by
NWPs. If it is not appropriate or
practicable to require compensatory
mitigation for a particular activity, and
that activity will result in minimal
adverse effects on the aquatic
environment, then the district engineer
may determine that compensatory
mitigation is not necessary. Otherwise,
if the proposed activity will result in
more than minimal adverse effects on
the aquatic environment after
determining that compensatory
mitigation is not appropriate or
practicable, then an individual permit
would be required.
One commenter said that the NWPs
do not distinguish between different
types of waters, but combine waters
when applying the acreage limit for the
NWP. This commenter stated that the
Corps needs to recognize that different
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types of waters often have different
functions.
The NWPs do recognize different
types of waters. The terms and
conditions of NWPs are often based on
the characteristics of different types of
waters. For example, NWP 39 does not
authorize discharges of dredged or fill
into non-tidal wetlands adjacent to tidal
waters.
One commenter said that the
requirement for NWP activities to be
single and complete projects should not
be removed, citing the proposed
changes to NWPs 13, 15, 18, and 19.
This commenter stated that the
requirement for single and complete
projects does not appear outside of the
Corps definition at 33 CFR 330.2(i). One
commenter objected to the removal of
the requirement in several NWPs to
submit an avoidance/minimization
statement with the pre-construction
notification.
The requirement that NWPs authorize
single and complete projects applies to
all NWPs. Limiting the NWPs to
authorize only single and complete
projects is a long-standing practice, and
we are adding a new general condition
(GC 28) to clarify that the NWPs only
authorize single and complete projects.
The requirement for an avoidance/
minimization statement that was in
NWPs 39, 43, and 44 is not necessary,
because we have modified NWP 39 to
require pre-construction notification for
all activities, and we are requiring preconstruction notification for all
construction and expansion of storm
water management facilities under NWP
43. In addition, general condition 20
requires permittees to avoid and
minimize adverse effects to waters of
the United State to the maximum extent
practicable on the project site. When
reviewing a pre-construction
notification, the district engineer will
determine whether sufficient avoidance
and minimization of impacts to waters
of the United States has occurred, and
whether the activity complies with
general condition 20. It is the
responsibility of the district engineer to
make this determination, and we do not
believe it is appropriate to place that
burden on the prospective permittee by
requiring the submittal of a statement
with the pre-construction notification.
One commenter recommended that
the Corps adopt an administrative
appeal process for activities authorized
by NWPs, which would provide for
third party appeals. Another commenter
said that compliance inspections should
be conducted for a certain number of
NWP activities per year. One
commenter said that the Corps needs to
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do more enforcement and monitoring of
activities authorized by NWPs.
We do not believe it would be
appropriate or necessary to establish an
administrative appeal process for the
NWP program, since the NWPs
authorize only those activities that have
minimal individual and cumulative
adverse effects on the aquatic
environment. The administrative appeal
process at 33 CFR part 331 applies only
to individual permits and jurisdictional
determinations, and does not provide
for third party administrative appeals.
Performance measures established for
the Regulatory Program require our
district offices to conduct compliance
inspections for a proportion of general
permit activities occurring in a given
year.
One commenter said that the Corps
should retain a separate NWP for
aggregate mining activities (the current
NWP 44), and provide greater acreage
limits, since the proposed modification
of NWP 44 will have little utility for the
aggregate mining industry.
We do not believe it would be
appropriate to issue another NWP for
aggregate mining activities, with greater
acreage limit. The acreage limit for NWP
44 is intended to ensure that this NWP
authorizes only those activities with
minimal individual and cumulative
adverse effects on the aquatic
environment. This NWP authorizes
aggregate mining activities.
Two commenters said that all
references to excavation in the NWPs
should cite 33 CFR 323.3(d) to clarify
that not all excavation activities require
section 404 permits. One commenter
suggested adding a new general
condition which would require
submittal of a delineation of nonjurisdictional wetlands with the preconstruction notification for those
NWPs authorizing development
activities, so that states could be
notified of these activities. One
commenter said that NWPs should not
authorize activities in springs, seeps,
headwater streams, and fens.
Many excavation activities result in
discharges of dredged material that
require section 404 permits. When
reviewing pre-construction
notifications, district engineers will
determine whether an excavation
activity results in a discharge of dredged
material and requires a section 404
permit, or whether a permit is not
needed. It is not appropriate for the
Corps to require prospective permittees
to submit delineations of areas that are
not waters of the United States with
their pre-construction notifications.
States that regulate these nonjurisdictional aquatic habitats should
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address those concerns through their
permit processes. The NWPs can be
regionally conditioned to restrict or
prohibit NWP activities in springs,
seeps, headwater streams, and fens.
One commenter requested that the
Corps reissue NWP 26, which
authorized discharges into headwaters
and isolated waters, in accordance with
the limits described in the December 13,
1996 Federal Register notice.
There are no plans to reissue NWP 26.
This NWP expired on June 7, 2000. We
have issued NWPs that have replaced
NWP 26.
Water Quality Certification/Coastal
Zone Management Act Consistency
Determination Issues
One commenter said that the Corps
should provide an opportunity for state
and Tribal water quality certification
agencies to participate early in the NWP
reissuance process, to reduce potential
conflicts during the water quality
certification process. Another
commenter requested clarification
regarding enforcement of the NWPs, in
cases where a provisional NWP
verification is issued, but the permittee
proceeds with work without receiving
the individual water quality
certification. This commenter asked
whether the Corps or the state would
initiate an enforcement action. One
commenter objected to use of
provisional NWP verifications in cases
where water quality certification has not
yet been issued for a particular NWP
activity.
We cannot begin coordination for
water quality certification at an earlier
time in the NWP reissuance process.
States and Tribes need to see the
proposed permit and general condition
language, which is not available until
the publication of the proposal in the
Federal Register, in order to proceed
with the certification process. We
believe there is generally adequate time
to complete the water quality
certification process, however, where
there is not, the Corps will issue only
provisional verifications until the State
or Tribe has completed its certification
process; in this case, permittees are
required to obtain individual
certification directly from the State or
Tribe before commencing work.
If a provisional NWP verification is
issued, the activity is not authorized by
NWP until the required water quality
certification is obtained or waived. If the
project proponent begins the work
before water quality certification is
obtained or waived, the district engineer
has full authority to initiate an
enforcement action for the discharge of
dredged or fill material into waters of
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the United States without a valid
permit, in violation of the Clean Water
Act. The district engineer will use his or
her discretion, when determining
whether to pursue an enforcement
action. The use of provisional NWP
verifications is necessary to provide
timely responses to prospective
permittees in cases where the State or
Tribe has not yet completed its
certification process. In addition, some
States prefer not to issue general
certifications for some or all NWPs.
These States require a review of
individual PCNs before issuing water
quality certification for a particular
activity.
Discussion of Comments and Final
Permit Decisions
Nationwide Permits
NWP 1. Aids to Navigation. There
were no changes proposed for this NWP,
and no comments were received. This
NWP is reissued without change.
NWP 2. Structures in Artificial
Canals. There were no changes
proposed for this NWP, and no
comments were received. This NWP is
reissued without change.
NWP 3. Maintenance. We proposed to
modify this NWP by removing the
provisions for the restoration of uplands
damaged by discrete events. We also
proposed to add maintenance dredging
or excavation of intakes, outfalls, and
canals, which was authorized by NWP
7.
Several commenters expressed
support for the proposed changes to this
NWP. One commenter objected to the
removal of the explicit references to the
‘‘water quality’’ and ‘‘management of
water flows’’ general conditions, stating
that the removal of those references
would change the intent of the NWP.
One commenter recommended
removing the language regarding the
disposal of excavated material in upland
areas, since it implies that excavation
activities are regulated by the Corps
under Section 404 of the Clean Water
Act. Several commenters recommended
adding language to clarify that
excavation activities, or incidental
fallback, do not require a section 404
permit. One commenter said that the
definition of ‘‘currently serviceable’’
should remain in the text of this NWP,
instead of moving it to the ‘‘Definitions’’
section.
Even though explicit references to
general conditions were removed from
its text, all general conditions, including
those general conditions cited above, are
still applicable to this NWP. The terms
of this NWP require permittees to
deposit and retain dredged or excavated
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materials in an upland area, unless the
district engineer authorizes the use of
another area. This term does not suggest
that excavation activities not involving
discharges of fill or dredge material into
Section 404 waters are regulated by the
Corps. Instead, it specifies the type of
site that may receive dredged or
excavated material under this NWP for
activities that do require Section 404
authorization. Excavation activities in
waters of the United States require
section 404 permits if they result in a
discharge of dredged or fill material into
those waters (see 33 CFR 323.2(d)).
Activities that result in only incidental
fallback do not require permits. Since
the definition of ‘‘currently serviceable’’
is used in NWPs 41 and 47, it is more
appropriate to have the definition in the
‘‘Definitions’’ section, for easier
reference.
A couple of commenters objected to
moving the provision authorizing the
repair, rehabilitation, or replacement of
structures or fills destroyed or damaged
by discrete events to proposed NWP A,
which requires pre-construction
notification for all activities. These
commenters said that the proposed
change would hinder the ability of
utility companies and transportation
departments to quickly repair utility
lines, roads, and other important
infrastructure damaged or destroyed by
severe storms. One commenter
suggested adding another note to this
NWP, to refer potential applicants to
NWP 45 in cases where structures that
have been made non-functional by some
discrete event may qualify for repair,
rehabilitation, or replacement.
We have restored the language
authorizing the repair, rehabilitation, or
replacement of structures or fills
destroyed or damaged by storms or
other discrete events in paragraph (a) of
NWP 3, and removed it from proposed
NWP A (now designated as NWP 45).
Because of this change, it is no longer
appropriate to add a note to this NWP
to refer to NWP 45.
One commenter suggested that this
NWP should not be used to authorize
additional or new work, fill, riprap or
structures that was not part of the
original authorization. One commenter
stated that the continued maintenance,
repair, restoration, and replacement of a
structure may represent ongoing
impacts that are more than minimal,
and may preclude restoration of
environmental features at the project
site. This commenter said that those
types of activities should require ongoing mitigation. Another commenter
said that this NWP should not be
reissued, since its use results in more
than minimal adverse impacts to the
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aquatic environment. Another
commenter suggested that this NWP
should not authorize replacement of
structures and fill, and that it should be
restricted to repair or rehabilitation
activities involving 50 percent or less of
a structure. One commenter said that
this NWP should authorize
modifications to older structures that
would help improve the aquatic
environment. This commenter also
recommended replacing the use of
riprap with less environmentally
damaging alternatives, such as
bioengineered structures.
This NWP does not authorize any
significant increase in the original
structure or fill. Only minor deviations
necessary to conduct repairs and
maintenance, or the placement of the
minimum necessary riprap to protect
the structure, are eligible for
authorization under this NWP. Because
of the nature of activities authorized by
this NWP, as a general rule
compensatory mitigation should not be
required for these maintenance
activities. If a Department of the Army
permit was required to construct the
original structure or fill, appropriate
compensatory mitigation would have
been required by the district engineer
when the permit was issued, to offset
the loss of aquatic resource functions
and services resulting from the
authorized work. Additional
compensatory mitigation is usually
unnecessary to maintain those
structures or fills. The terms and
conditions for NWP 3, plus any regional
conditions imposed by division
engineers, will ensure that this NWP
authorizes only those activities with
minimal individual and cumulative
adverse effects on the aquatic
environment. We believe that this NWP
should continue to authorize the
replacement of structures or fills, or
rehabilitation activities, since those
activities usually result in minimal
adverse effects on the aquatic
environment. As for modifying this
NWP to authorize changes to structures
that would improve the aquatic
environment, we believe it would be
more appropriate for district engineers
to authorize such changes through other
permits. Changes to structures would
require more thorough evaluation to
ensure that net improvements to the
aquatic environment will occur. The use
of bioengineering methods to protect
existing structures may not be very
effective, because of the environmental
conditions, such as water flows, near
these structures. Riprap is usually the
most effective means of protecting these
structures, and the terms of this NWP
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require minimization of the footprint of
the riprap. District engineers can
consider bioengineering on a case-bycase basis, and authorize such activities
as appropriate.
One commenter said that this NWP
should not authorize the maintenance of
bank stabilization structures that are
more than 300 feet long. One
commenter suggested dividing
paragraph (b) into two subparagraphs.
One subparagraph would authorize
debris and sediment removal and the
other subparagraph would authorize
riprap. This commenter also indicated
that this NWP should be modified to
limit the removal of sediment to the
minimum necessary to ‘‘restore the bed
of the waterway to its natural grade.’’
This NWP authorizes only activities
that repair or return an activity to
previously existing conditions. We do
not believe it is necessary to further
restrict this NWP to limit maintenance
of bank stabilization structures.
Dividing paragraph (b) into two
subparagraphs is not needed, since the
riprap is typically used to protect the
structure once the accumulated
sediment has been removed. The
purpose of this NWP is to authorize
restoring structures or fills to their
original condition. It may not be
possible to determine the ‘‘natural
grade’’ of the waterway, and this may
not have been the condition at the time
the structure or fill was originally
authorized. Therefore, we believe the
current language is more appropriate.
Several commenters recommended
modifying this NWP to authorize both
permanent and temporary impacts of
maintenance activities, since the
requirement to submit a preconstruction notification for temporary
impacts would significantly increase
regulatory and administrative burdens
on the applicants and the Corps,
without any environmental benefits or
added value to the process.
We agree, and have added a new
paragraph (c) to this NWP to address
temporary structures, fills, and work
necessary to conduct the maintenance
activities authorized by this NWP.
Several commenters objected to the
requirement to provide information
about original design capacities and
configurations of the structures and
canals as part of the pre-construction
notification for the proposed activity.
These commenters stated that this
information may not exist or be readily
available, particularly for old facilities
and structures. These commenters
recommended that the information be
required only where it is reasonably
available. Alternatively, the commenters
proposed retaining the language
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regarding the project not causing more
than minimal changes to the flow
characteristics of the stream, or
increased flooding, instead of
specifically requiring original design
information.
The provision to require information
regarding the original design capacities
and configurations of structures and
other features is only applicable when
maintenance dredging is proposed. We
believe that this information can be
developed fairly easily, since the
capacities and configurations of the
outfalls, intakes, impoundments, and
canals can be developed or inferred by
examining the existing facilities, in
cases where historical documentation is
not available.
Several commenters expressed
opposition to the terms of the NWP that
limit the removal of sediment to the
minimum necessary to restore the
waterway to the approximate
dimensions that existed when the
structure was built. Another commenter
recommended changing the language to
require restoration of the project to its
original design conveyance capacity.
The current language is adequate to
ensure that this NWP authorizes
necessary sediment removal activities
that result in minimal adverse effects on
the aquatic environment. We believe
that the limits for the removal of
sediments should be established with
regard to the conditions of the waterway
itself at the time of project construction
rather than to the specifications of the
structures.
One commenter requested
clarification as to whether the 200 foot
limit on the removal of accumulated
sediment is subject to the 1⁄2 acre limit
found in other NWPs.
This NWP does not have a 1⁄2 acre
limit. If this NWP is used with another
NWP to authorize a single and complete
activity, then the activity is subject to
the requirements of general condition
24, Use of Multiple Nationwide Permits.
If this NWP is used with an NWP with
a 1⁄2 acre limit, such as NWP 39, then
the 1⁄2 acre limit would apply to the
single and complete project.
One commenter requested the
addition of ‘‘flood conveyance
channels’’ to paragraph (b) of this NWP,
instead of requiring the use of NWP 31.
Another commenter stated that
additional routine maintenance
activities, which are authorized by
NWPs 31 and 43, should be
consolidated under NWP 3. One
commenter suggested adding language
to clarify that this NWP authorizes
emergency repairs of submarine fiber
optic cables.
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NWP 31 is being reissued to authorize
maintenance activities for existing flood
control facilities, including flood
conveyance channels. Therefore, we do
not believe it is necessary to modify
NWP 3 to authorize those activities. We
are also reissuing NWP 43 to authorize
maintenance activities for storm water
management facilities. Emergency
repairs of submarine fiber optic cables
may be authorized by this NWP,
provided the activity meets its terms
and conditions.
One commenter indicated that small
sediment removal projects should not
require pre-construction notification.
Another commenter stated that preconstruction notification should not be
required for the placement of riprap to
protect structures. A few other
commenters said that pre-construction
notification should not be required for
activities authorized by paragraph (b) of
this NWP. In contrast, one commenter
suggested that pre construction
notification should be required for all
activities covered under NWP 3.
We believe that the pre-construction
notification requirements for this NWP
are appropriate. Pre-construction
notification is required for those
activities that may have the potential to
cause more than minimal adverse effects
on the aquatic environment.
One commenter recommended that
sediments should be sampled to project
depth prior to dredging, and that sandy
sediment suitable for nearshore disposal
should be returned to the littoral system
down drift of the project site.
Regulatory Guidance Letter 06–02
establishes that testing of dredge
material is not required when there is
reason to believe that no contaminants
are present in the material. Therefore, a
standard requirement to sample and test
sediments to be dredged under NWP 3
would not be appropriate. The
nearshore disposal of sandy sediments
should be addressed through separate
authorizations, such as individual
permits, since those activities may have
more than minimal adverse
environmental effects.
One commenter indicated that
significant wetland habitat development
has been observed on sediments left in
place for many years within canals
associated with outfall and intake
structures. That commenter stated that
exempting maintenance activities in
such canals from the 200 linear foot
restriction may have a significant
impact on the wetland habitats in these
channels. Another commenter suggested
that the placement of riprap or any other
bank stabilization material in, or the
removal of accumulated sediment from,
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any special aquatic site should be
prohibited.
Since this NWP only authorizes
activities that restore an area to its
previous condition, we do not believe it
is appropriate to prohibit the
maintenance of structures or fills simply
because a special aquatic site may have
formed in these areas. District engineers
will review pre-construction
notifications to determine if the
placement of riprap or the removal of
accumulated sediments in special
aquatic sites would cause more than
minimal impact, and use discretionary
authority to address situations where
they would.
One commenter stated that affected
tribes should be informed of all preconstruction notifications for this NWP
that involve in-water work and be
provided 30 days to provide comments.
This commenter also suggested that
while bioengineered projects are less
environmentally damaging than riprap
and offer benefits to salmon, the
presence of wood in some bank
protection structures has the potential to
interfere with treaty fishing access by
preventing the use of nets.
Coordination of proposed NWP 3
activities with Indian tribes is more
appropriately addressed through
government-to-government
consultations with Corps districts.
General condition 16, Tribal Rights,
does not allow an activity or its
operation to impair reserved tribal
rights, including but not limited to,
reserved water rights and treaty fishing
and hunting rights. Compliance with
this general condition, along with
coordination with interested Indian
Tribes, will help protect tribal rights.
One commenter suggested that the
placement of riprap should be the
minimum necessary to protect the
structure, in order to reduce adverse
effects to habitat-forming processes
within waterbodies, such as salmon
habitat. Another commenter said that
this NWP should not authorize
maintenance work on culverts that fail
to meet appropriate standards for the
upstream and downstream passage of
fish, or culverts that do not allow for the
downstream passage of substrate and
wood.
The terms and conditions of this NWP
limit the placement of riprap to the
minimum necessary to provide adequate
erosion protection. Other NWP general
conditions, such as general condition 17
for endangered species, may provide
additional protection for species of
concern, as well as their habitat. General
condition 2 prohibits activities which
could disrupt the necessary life cycle
movements of aquatic species.
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One commenter stated that preconstruction notifications should be
required for all NWP 3 activities to
ensure compliance with its terms and
conditions. Another commenter stated
that the Corps should carefully review
all maintenance applications to ensure
that the area impacted is not larger than
needed to complete the maintenance
activities, and that no additional
impacts are authorized or conducted.
We do not agree that pre-construction
notification should be required for all
activities. The terms and conditions of
this NWP are adequate to ensure that it
authorizes only those activities with
minimal adverse effects on the aquatic
environment. Where there are concerns
for the aquatic environment, division
engineers can regionally condition this
NWP to require pre-construction
notification or other measures.
One commenter said that streams near
roads may migrate from their original
location and compromise the road. This
commenter said that for those
situations, this NWP should authorize
relocation of the stream back to its
original location. The commenter also
indicated that small channel
realignments should be authorized to
properly convey the water into culverts.
This NWP does not authorize new
stream channelization or stream
relocation projects. Those activities may
be authorized by other Department of
the Army permits.
This NWP is reissued with the
modifications discussed above.
NWP 4. Fish and Wildlife Harvesting,
Enhancement, and Attraction Devices
and Activities. We proposed to remove
the provision for shellfish seeding, since
we proposed to modify NWP 27 to
authorize this activity. No comments
were received. This NWP is reissued as
proposed.
NWP 5. Scientific Measurement
Devices. We proposed to remove the
pre-construction notification
requirement for discharges of 10 to 25
cubic yards for the construction of small
weirs and flumes, but retain the 25
cubic yard limit for such construction.
Several commenters supported this
NWP and the proposed removal of the
pre-construction notification
requirement on the basis that activities
authorized under this NWP result in
minimal impacts. Another commenter
agreed with the removal of the preconstruction notification requirement
for discharges of 10 to 25 cubic yards for
construction of weirs and flumes
because it will facilitate the
implementation of water quality
improvement projects sponsored by
Federal, State, and local agencies, as
well as the scientific community. Two
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commenters objected to the removal of
the pre-construction notification
threshold. One commenter
recommended conditioning this NWP to
ensure that authorized activities do not
interfere with the movements of
organisms within watercourses or
prevent ingress or egress of aquatic
organisms.
Based on our past experience with
this NWP, we believe the removal of the
pre-construction notification
requirement for discharges of 10 to 25
cubic yards for the construction of small
weirs and flumes is appropriate. Project
proponents are required to comply with
all applicable general conditions,
including general condition 2, Aquatic
Life Movements, which prohibits
activities from substantially disrupting
life cycle movements of aquatic
organisms. Further, we believe the
district engineer’s authority to issue
case-specific special conditions and to
impose regional conditions to require
pre-construction notifications for certain
activities, such as activities involving
specified quantities of fills for the
construction of small weirs and flumes,
is adequate to address local concerns
regarding potential adverse effects to the
movement of aquatic organisms.
One commenter said that the NWP
should have a condition requiring all
temporary devices to be removed when
the devices will no longer be used. This
commenter also asked whether this
NWP authorizes the installation of
single measurement devices or multiple
measurement devices.
The removal of temporary fills is
required by general condition 13. The
NWP authorizes single and complete
scientific measurement device projects.
Scientific measurement devices with
independent utility can be authorized
by separate NWP authorizations.
This NWP is reissued as proposed.
NWP 6. Survey Activities. We
proposed to modify this NWP to add
exploratory trenching to the list of
authorized activities and to authorize
the construction of temporary pads used
for survey activities, provided the
discharge does not exceed 25 cubic
yards.
Two commenters supported the
proposed modifications and one
commenter said that the NWP would
result in more than minimal impacts to
the aquatic environment. One
commenter stated that there should be
a 1⁄4 acre limit for exploratory trenching.
This commenter also suggested
imposing a 25 cubic yard limit on all
activities authorized by this NWP.
It has been our experience that
exploratory trenching results in minimal
adverse effects on the aquatic
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environment, and this NWP has been
conditioned to require restoration of the
trenched area upon completion of work.
Since most impacts associated with
exploratory trenches are temporary, an
acreage limit is not necessary. Division
engineers may impose regional
conditions to require pre-construction
notifications or specific limits for
certain activities. District engineers may
also exercise discretionary authority and
require an individual permit if a
proposed activity would result in more
than minimal adverse effects on the
aquatic environment. It is unnecessary
to impose a 25 cubic yard limit on all
discharges authorized by this NWP,
since most of these discharges are
temporary. Temporary fills must be
removed upon completion of the work,
in accordance with the requirements of
general condition 13. Any permanent
fills are likely to be small in size,
because of the types of activities
authorized by this NWP.
One commenter suggested adding
language regarding the backfilling of the
exploratory trench. Some commenters
stated that the definition of ‘‘exploratory
trenching’’ should include more
prescriptive details such as benchmarks,
width, and depth.
We are conditioning this NWP to
require permittees to backfill the top 6
to 12 inches of exploratory trenches
constructed in wetlands with topsoil
from the trench. This change will bring
consistency with the terms of other
NWPs that authorize trenching
activities. We do not believe that it is
necessary to include prescriptive limits
on the trench dimensions. However,
division engineers may choose to
establish such limits through regional
conditions.
One commenter suggested that the 25
cubic yard limit for discharges
associated with temporary pads should
be removed. Another said that the 25
cubic yard limit should apply to the
cumulative amount of material for
multiple drill sites. Two commenters
said that limits should be placed on the
amount of such discharges because a
state may not issue water quality
certification for this NWP.
The 25 cubic yard limit is necessary
to help ensure that the NWP authorizes
only activities with minimal adverse
effects on the aquatic environment. It
also provides a suitable limit on the
quantity of discharge necessary for
construction of these temporary pads.
The cubic yard limit for temporary pads
applies to a single and complete project,
as defined at 33 CFR 330.2(i). If a state
does not issue water quality certification
for this NWP, an individual water
quality certification must be obtained or
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waived for each activity before it is
authorized in that state.
One commenter stated the NWP
should also authorize temporary access
roads. Such work may qualify for the
404(f) exemption for temporary mining
roads or could be authorized by NWP
33.
The NWP is reissued with the
modification discussed above.
NWP 7. Outfall Structures and
Associated Intake Structures. We
proposed to move maintenance
dredging and excavation activities to
NWP 3. We also proposed to change the
title of this NWP to more clearly
describe what it authorizes.
Several commenters supported
moving maintenance dredging and
excavation activities to NWP 3, while
one commenter objected to the proposed
change. One commenter said this NWP
should require pre-construction
notification only for section 10
activities, since Clean Water Act
authorization for these structures is
already provided through the permit
process under Section 402 of the Clean
Water Act. One commenter stated that
construction and maintenance of outfall
structures should not include bank
stabilization structures.
Outfall structures and associated
intake structures require section 404
authorization if they involve discharges
of dredged or fill material into waters of
the United States. Sections 404 and 402
of the Clean Water Act address different
types of discharges. In addition, the
permitting criteria under section 404
differ from those of section 402. In
addition, some activities authorized by
this NWP may be exempt from section
402 permit requirements. The preconstruction notification requirement is
necessary to ensure that activities
authorized by this NWP will have no
more than minimal adverse impacts to
the aquatic environment. Bank
stabilization activities are not
authorized by this NWP but may be
authorized by NWP 13 or other types of
permits.
One commenter suggested adding a
provision to require intake structures
constructed for withdrawing cooling
water to adhere to requirements
contained in Section 316(b) of the Clean
Water Act. Another commenter
suggested that this NWP should include
a reference to the U.S. Environmental
Protection Agency’s section 316(b)
implementation initiative and require
incorporation of Best Technology
Available methods developed from this
initiative. This commenter also said that
intake structures should utilize passive
screens with openings not to exceed one
centimeter (or one millimeter in waters
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having anadromous fish), with a
maximum intake velocity of 0.5 feet per
second.
Section 316(b) of the Clean Water Act
is implemented through (and only
applies to) permits issued pursuant to
Section 402. Thus, any structure that is
in compliance with regulations issued
under the NPDES program (Section 402)
must also be in compliance with
regulations issued under Section 316(b).
Specific suggestions regarding
technology choices for intake structures
are more appropriately addressed
through other permit authorities, such
as the 402 program. Activities
authorized by this NWP may require
other Federal, State, or local permits or
licenses.
One commenter suggested adding
modifications of existing intakes as an
authorized activity, for cases where
intake structure modifications are
required by rules recently promulgated
under Section 316(b) of the Clean Water
Act. Another commenter recommended
adding a note to refer applicants to NWP
3 for future maintenance activities.
In the first sentence of this NWP, we
have added the phrase ‘‘or
modification’’ after the word
‘‘construction. It is important to note
that this NWP only authorizes the
construction or modification of intake
structures that are associated with
outfall structures. This would include
cooling water intake structures where
the heated cooling water is subsequently
discharged back into the waterbody
from which is was withdrawn. Adding
a note referencing NWP 3 for future
maintenance activities is inappropriate,
since there may be outfall structure
maintenance activities that do not
qualify for NWP 3 authorization.
One commenter requested
clarification that this NWP authorizes
only those activities that require permits
under Section 404 of the Clean Water
Act and/or Section 10 of the Rivers and
Harbors Act of 1899. This commenter
said that the current text of this NWP
indicates that all outfall and associated
intake structures that require section
402 permits would also require an NWP
authorization.
This NWP authorizes outfall
structures and associated intake
structures that require authorization
under Section 404 of the Clean Water
Act and/or Section 10 of the Rivers and
Harbors Act of 1899. If the construction
or modification of an outfall structure or
associated intake structure that requires
a section 402 permit does not involve
discharges of dredged or fill material
into waters of the United States or
structures or work in navigable waters
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of the United States, then a Corps
permit is not required.
One commenter recommended
conditioning this NWP to require intake
structures to be marked in a manner that
will reduce hazards to navigation during
and after construction. Another
commenter said that this NWP should
not authorize dredging operations
during fish spawning seasons. One
commenter said that this NWP should
prohibit the stockpiling of excavated
materials where sediment may erode to
surface waters. A commenter asserted
this NWP should be conditioned to
prohibit exposure of surface waters to
wet concrete, which may be toxic to
aquatic organisms.
General condition 1 states that any
safety lights and signals prescribed by
the U.S. Coast Guard, through
regulations or otherwise, must be
installed and maintained. This
condition adequately addresses
potential hazards to navigation.
Maintenance dredging associated with
outfall structures and their intake
structures may be authorized by NWP 3
or another type of permit. General
condition 3 states that activities in
spawning areas that occur during the
spawning seasons must be avoided to
the maximum extent practicable.
General condition 12 addresses
requirements for soil erosion and
sediment controls. Although concrete
may be toxic under certain
circumstances, it is generally not
considered to have toxic pollutants
present in toxic amounts. Therefore, its
use is not generally prohibited by
general condition 6, Suitable Materials.
One commenter said that agency
coordination should be required for the
construction of intake structures,
because those structures may impinge
and entrain larval fish.
We do not believe it is necessary to
require agency coordination for the
construction of intake structures. For
cooling water intake structures, this
issue is already addressed by the
Section 402 program. For other types of
intakes, it would be more appropriate to
address concerns regarding the
impingement and entrainment of larval
fish through regional conditions or
special conditions. Division and district
engineers, in consultation with resource
agencies, can develop species-specific
regional or special conditions to protect
larval fish.
This NWP is reissued with the
modification discussed above.
NWP 8. Oil and Gas Structures on the
Outer Continental Shelf. We proposed
to clarify that pre-construction
notification is required for all activities
authorized by this NWP. No comments
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were received. This NWP is reissued as
proposed.
NWP 9. Structures in Fleeting and
Anchorage Areas. There were no
changes proposed for this NWP. One
commenter said that moorage structures
may preclude the continued exercise of
Tribal fishing rights. This commenter
also asked that the Corps consult with
Indian Tribes that utilize these areas for
fishing, and requested that preconstruction notification be required for
all activities authorized by this NWP.
General condition 16 states that NWP
activities cannot impair reserved tribal
rights. Division and district engineers
can consult with Tribes to develop
regional conditions that will further
ensure that tribal rights are not impaired
by this NWP. Division engineers can
regionally condition this NWP to
require coordination with Tribes when
proposed activities may affect Tribal
lands or trust resources.
The NWP is reissued without change.
NWP 10. Mooring Buoys. There were
no changes proposed for this NWP. One
commenter stated that individual
mooring buoys can interfere with the
exercise of Tribal fishing rights and
should not be authorized by NWP. This
commenter also said that preconstruction notification should be
required for all activities authorized by
this NWP, and the Corps should consult
with Indian Tribes with usual and
accustomed fishing grounds. Another
commenter suggested limiting mooring
buoys to areas outside of Federal
navigation channel or dredged material
placement areas.
General condition 16 states that NWP
activities cannot impair reserved tribal
rights. Division and district engineers
can consult with Tribes to develop
regional conditions that will ensure that
tribal fishing rights are not impaired by
activities authorized by this NWP.
District and division engineers will
consider the need to add regional
conditions or case-specific conditions
where necessary to protect tribal rights.
Prohibiting the placement of mooring
buoys in Federal navigation channels or
dredged material placement areas is not
desirable. There are occasions where it
may be appropriate to place mooring
buoys in these areas on a permanent or
temporary basis, where the adverse
effects on navigation and other public
interest review factors are minimal.
Mooring buoys authorized by this NWP
must comply with general condition 1,
Navigation. Division engineers may also
add regional conditions to this NWP to
prohibit the placement of mooring
buoys in certain Federal navigation
channels or other areas of concern.
The NWP is reissued without change.
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NWP 11. Temporary Recreational
Structures. There were no changes
proposed for this NWP. One commenter
suggested that temporary buoys,
markers, small floating docks, and
similar structures can interfere with the
exercise of treaty fishing access and,
therefore, in an area subject to treaty
fishing, notification to affected tribes is
required. The commenter further stated
that regional conditions should be
added to require that such structures
shall be removed from salmon spawning
areas prior to commencement of the
spawning season. Another commenter
suggested that temporary recreation
structures may come into conflict with
Tribal fisheries and that preconstruction notification should be
required. In addition, consultation with
Indian Tribes with usual and
accustomed fishing grounds in the area
should also be conducted.
This NWP cannot authorize any
activity that may impair reserved tribal
rights, including, but not limited to,
reserved water rights and treaty fishing
and hunting rights (see general
condition 16). District and division
engineers will consider the need to add
regional conditions or case-specific
conditions where necessary to protect
such tribal rights.
One commenter recommended
conditioning the NWP to require
temporary recreation structures to be
removed within seven days after the use
has been discontinued, instead of the 30
days specified in the NWP. One
commenter asserted that the required
approval from the reservoir manager
should be in writing.
Shorter time periods for removal can
be imposed through regional
conditioning, or through special
conditions provided in NWP
verifications. The process for approving
buoys or markers at Corps of Engineers
reservoirs is at the discretion of the
reservoir manager.
The NWP is reissued without change.
NWP 12. Utility Line Activities. We
proposed to modify this NWP by
removing the provisions authorizing the
construction of permanent and
temporary access roads and simplifying
the pre-construction notification
thresholds. Several commenters
supported all proposed changes to this
NWP.
One commenter recommended
modifying this NWP to explicitly
include utility line relocation, in
addition to utility line construction,
maintenance, and repair. Two
commenters suggested reducing the
authorized duration of temporary
sidecasting. One of these commenters
said that four weeks is sufficient time
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for temporary sidecasting, and the other
commenter recommended a time limit
of 30 days. One commenter said that
this NWP should require all trenched
material to be returned to the trench as
backfill, not just the upper 6 to 12
inches, to sustain groundwater
hydrology and prevent drainage of
wetlands and other waters of the United
States. One commenter requested that
total impacts at the site be limited to 3⁄10
acre.
This NWP authorizes the relocation of
utility lines, which is covered by the
construction, maintenance, and repair
activities authorized by this NWP. We
believe that three months is an
appropriate time frame for temporary
sidecasting of excavated material into
waters of the United States. Division
engineers can regionally condition this
NWP to reduce the authorized period of
temporary sidecasting, to further ensure
minimal adverse effects. In response to
a pre-construction notification, district
engineers can add special conditions to
the NWP authorization to reduce the
length of time temporary sidecasting is
authorized. We do not agree that it is
necessary to require that all trenched
material be returned to the trench to
maintain pre-construction hydrology.
The NWP explicitly prohibits
backfilling the trench in a manner that
would result in a french drain effect,
and drain nearby waters. We believe the
1/2 acre limit for this NWP is sufficient
to ensure that it authorizes only those
activities that result in minimal
individual and cumulative adverse
effects on the aquatic environment. This
limit applies to the total discharges
associated with the single and complete
project.
Several commenters supported the
proposed pre-construction notification
thresholds for this NWP, stating that
they are simpler than the current
thresholds and would capture many of
those utility line activities that required
pre-construction notification under the
2002 NWP. A couple of commenters
recommended retaining the preconstruction notification thresholds of
the NWP 12 issued in 2002. A number
of commenters said that the preconstruction notification for temporary
losses of greater than 1⁄10 acre of water
of the United States should be
eliminated. Some of these commenters
stated that this pre-construction
notification threshold is confusing,
because it is not consistent with the
definition of ‘‘loss of waters of the
United States.’’ Other commenters
recommended changing the phrasing of
this pre-construction notification
threshold from ‘‘temporary loss’’ to
‘‘temporary impact’’ to provide
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consistent terminology for the NWPs.
Several commenters said that the 1⁄10
acre pre-construction notification
threshold for temporary losses should
be eliminated, because it is not
necessary to ensure minimal adverse
effects and it is not consistent with the
pre-construction notification thresholds
of other NWPs. One commenter
indicated that the pre-construction
notification threshold for temporary
losses would result in a dramatic
increase in the numbers of preconstruction notifications submitted to
the Corps. Another commenter stated
that this pre-construction notification
threshold would remove incentives for
project proponents to minimize
temporary impacts. Several commenters
said that requiring pre-construction
notifications for temporary losses
greater than 1⁄10 acre would increase the
number of wetland delineations
required to be submitted with those
notifications.
One commenter asked if an activity
resulting in impacts of 1⁄10 acre or less
to special aquatic sites, including
wetlands, would require preconstruction notification. Another
commenter said that there may be utility
line activities resulting in the loss of
less than 1⁄10 acre that may result in
more than minimal adverse effects on
the aquatic environment. One
commenter objected to the removal of
the pre-construction notification
requirement for activities that include
mechanized landclearing of forested
wetlands, stating that this may result in
significant habitat loss of forested
wetlands and a significant permanent
loss of forested wetland functions. One
commenter recommended requiring preconstruction notifications for activities
that may impact fish passage.
We are restoring the pre-construction
notification thresholds that were in the
NWP 12 issued in 2002, so that district
engineers will be able to conduct caseby-case review for certain utility line
activities that have the potential to
result in more than minimal adverse
effects on the aquatic environment. Preconstruction notification will be
required if any of the following criteria
are met: (1) The activity involves
mechanized land clearing in a forested
wetland for the utility line right-of-way;
(2) a section 10 permit is required; (3)
the utility line in waters of the United
States, excluding overhead lines,
exceeds 500 feet; (4) the utility line is
placed within a jurisdictional area (i.e.,
water of the United States), and it runs
parallel to a stream bed that is within
that jurisdictional area; (5) discharges
that result in the loss of greater than 1⁄10acre of waters of the United States; (6)
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permanent access roads are constructed
above grade in waters of the United
States for a distance of more than 500
feet; or (7) permanent access roads are
constructed in waters of the United
States with impervious materials.
Discharges resulting in temporary losses
of waters only will no longer trigger a
pre-construction notification
requirement, unless they trigger one of
the criteria above.
Division engineers can regionally
condition this NWP to require preconstruction notification for other
utility line activities, if there are
concerns for the aquatic environment or
public interest that warrant lower preconstruction notification thresholds,
such as endangered or threatened
species, or impacts to forested wetlands.
General condition 2, Aquatic Life
Movements, requires permittees to not
disrupt necessary life cycle movements
of aquatic organisms, such as fish.
Several commenters requested that
the definition of single and complete
project, as applied to utility line
projects, be modified to state that the
1⁄10 acre pre-construction notification
threshold applies to the entire utility
line and not to each separate water or
wetland crossing.
The requirement to submit a preconstruction notification for those
utility line activities listed in the
‘‘Notification’’ paragraph of this NWP
applies to a single and complete project,
as defined at 33 CFR 330.2(i). In the case
of a utility line, a single and complete
project consists of a single crossing of a
water of the United States, or more than
one crossing at the same location (see
the definition of ‘‘single and complete
project’’).
Several commenters expressed
opposition to the proposed removal of
access roads from this NWP, especially
the construction of temporary access
roads, which would require
authorization under NWP 33 and
require pre-construction notification for
all activities. One commenter supported
the use of NWPs 14 and 33 for utility
line access roads, because it would
provide greater flexibility in the
locations where these roads could be
built. Most of these commenters
expressed concern that requiring preconstruction notification for all
temporary access road construction
activities will significantly increase the
regulatory burdens on permittees and
most likely cause substantial delays in
utility line projects. One commenter
said that access roads should be
retained in this NWP, with a 1⁄2 acre
limit for the utility lines and a 1⁄2 acre
limit for the access road. Several
commenters stated that requiring
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authorization of permanent access roads
through NWP 14 could result in impacts
greater than 1⁄2 acre at the site of a single
and complete project. One commenter
said that utility line substations should
be authorized by another NWP, because
these facilities can be constructed at a
more distant location from the utility
line.
After considering these comments, as
well as the probable negative effects that
this proposed change would have on
essential services such as the
distribution of energy to the public, we
have decided to retain authorization of
permanent and temporary access roads
in NWP 12. We have added a paragraph
to authorize access roads, using
language from the NWP 12 issued in
2002. We are also putting Note 2 back
into this NWP. This note states that
access roads used for both construction
and maintenance are authorized by this
NWP. This note has been adapted from
the NWP 12 issued in 2002, but revised
to clarify that temporary access roads
may be authorized by NWP 12, provided
the area is restored to pre-construction
elevations and revegetated as
appropriate. To address concerns about
temporary impacts to waters of the
United States associated with utility
line activities, we are adding explicit
requirements to remove all temporary
fills in their entirety, return affected
areas to pre-construction elevations, and
revegetate affected areas as appropriate.
The 1⁄2 acre limit for this NWP applies
to each single and complete utility line
activity. There are not separate acreage
limits for utility lines and access roads.
Retaining authorization of access roads
in this NWP, as well as authorization for
utility line substations, will help
provide effective authorization for
utility line activities.
One commenter recommended
reformatting this NWP to be consistent
with other NWPs. Another commenter
suggested that the phrase ‘‘provided the
activity does not result in the loss of
greater than 1⁄2 acre of those waters’’ be
deleted, since the 1⁄2 acre limit is
indicated in the first paragraph of this
NWP. One commenter said that
mitigation should be required for all
NWP activities. Another commenter
stated that the NWP should clarify that
mitigation banks may be used to provide
compensatory mitigation for permanent
adverse effects authorized by this NWP.
The format of this NWP need not be
consistent with the other NWPs,
because of the authorized activities. We
are retaining the reference to the 1⁄2 acre
limit in the paragraph that authorizes
utility line substations, to make it clear
that any losses associated with this
activity are included in the 1⁄2 acre limit.
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A similar reference to the 1⁄2 acre limit
is also provided in the paragraph
authorizing access roads. Mitigation
requirements for this NWP will be
established in accordance with general
condition 20, Mitigation. This general
condition states that mitigation banks
may be used to provide compensatory
mitigation for activities authorized by
NWPs.
One commenter suggested adding
language to this NWP that would
require sand and gravel excavated from
a lake bed during trench excavation to
be temporarily sidecast in a manner
such that it would not be buried by
material with finer grain sizes. Another
commenter stated that this NWP should
not be used to authorize utility line
activities in streams that support
salmon.
Concerns for potential impacts to lake
substrate are more appropriately
addressed through either the special
conditions added to an NWP
authorization by the district engineer, or
by regional conditioning of the NWP by
division engineers. Potential impacts to
salmon are also more appropriately
addressed through regional conditions
or the review of pre-construction
notifications, including the district
engineer’s use of discretionary authority
and the addition of special conditions to
the NWP authorization.
One commenter said that this NWP
should be conditioned to require
placement of the utility line in the rightof-way of existing or proposed roads or
at the narrowest section of wetlands or
streams. This commenter also stated
that the number of stream crossings
should be limited to the minimum
necessary.
These concerns are addressed by
general condition 20, Mitigation, which
requires avoidance and minimization on
the project site to the maximum extent
practicable. It is not appropriate to
condition this NWP to require utility
lines to be placed in existing rights-ofway or at the narrowest sections of
waters of the United States. Often it is
not feasible to limit utility lines to these
areas, and practicable alternatives are
usually rather limited. Many utility
lines need to be installed in areas
without roads.
One commenter said that this NWP
should require communication or power
poles to be upgraded to current
standards to avoid detrimental impacts
to migratory birds. This commenter also
stated that this NWP should not
authorize wind generating turbines.
Design requirements for
communication or power poles relative
to migratory birds are more
appropriately addressed through other
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regulatory programs. Wind generating
turbines are not considered to be utility
lines. To the extent that the construction
of wind generating turbines requires
Department of the Army authorization,
those activities may be authorized by
individual permits, regional general
permits, or other NWPs (e.g., NWP 25).
NWP 12 is reissued with the
modifications discussed above.
NWP 13. Bank Stabilization. We
proposed to modify this NWP to
authorize bank stabilization activities in
special aquatic sites, provided the
prospective permittee submits a preconstruction notification.
Several commenters expressed
support for the proposed changes to this
NWP. Several commenters stated that
this NWP will result in more than
minimal adverse effects to the aquatic
environment, particularly for headwater
streams, and that individual permits
should be required for these activities.
Other commenters stated that the linear
limits of this NWP should be reduced
and that the waivers to the linear foot
and cubic yard limits should be
removed to ensure that the NWP
authorizes only those activities with
minimal adverse effects on the aquatic
environment. Several commenters
stated that bank stabilization projects in
excess of 500 feet or involving more
than one cubic yard per running foot
should be evaluated as individual
permits, with opportunity for public
review.
The terms and conditions of this
NWP, especially the pre-construction
notification requirements, will help
ensure that this NWP authorizes only
those activities that result in minimal
individual and cumulative adverse
effects on the aquatic environment. The
500 linear foot and the one cubic yard
limits must be waived in writing by the
district engineer, or the NWP cannot be
used to authorize activities that exceed
these limits. Bank stabilization activities
are often necessary to help protect
property, as well as water quality. In
response to a pre-construction
notification the district engineer can
add special conditions to the NWP
authorization to ensure minimal adverse
effects, or exercise discretionary
authority and require another type of
permit, such as an individual permit, for
the activity. Division engineers can
regionally condition this NWP to protect
high value waters and other important
resources.
One commenter recommended
modifying the text of this NWP to clarify
that authorized activities are not limited
to rivers and streams, but that this NWP
can also be used in coastal areas.
Several commenters stated that this
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NWP should not authorize impacts to
special aquatic sites. One commenter
recommended requiring a written
waiver from the district engineer to
authorize discharges of dredged or fill
material into special aquatic sites. A few
commenters said that mitigation should
always be required for activities
authorized by this NWP.
This NWP can be used to authorize
bank stabilization activities in all waters
of the United States, including rivers,
streams, and coastal areas. We do not
believe it is necessary to modify the text
of this NWP to list the types of
waterbodies in which it can be used.
Because many streams include or are
bordered by special aquatic sites,
precluding use of this permit in these
areas significantly limits its usefulness.
It may be beneficial to watersheds to
stabilize eroding banks, even though
small amounts of fringe wetlands or
mudflats may be impacted by a bank
stabilization activity. Therefore, bank
stabilization activities involving
discharges of dredged or fill material
into special aquatic sites may be
authorized by this NWP but preconstruction notification is required for
all such activities, which will provide
an opportunity for the district engineer
to review those activities to ensure that
any adverse effects on the aquatic
environment are minimal. For
additional assurance, we have added a
new paragraph (d) to require a written
waiver from the district engineer if the
activity involves discharges of dredged
or fill material into special aquatic sites.
If a written waiver is not issued by the
district engineer, then this NWP does
not authorize such discharges. In
response to a pre-construction
notification, the district engineer will
exercise discretionary authority if the
proposed bank stabilization activity is
in a special aquatic site and will result
in more than minimal adverse effects on
the aquatic environment. Division
engineers may also regionally condition
this NWP to prohibit discharges of
dredged or fill material into special
aquatic sites, where there are concerns
for the aquatic environment or other
public interest review factors.
We do not believe compensatory
mitigation should be required for all
bank stabilization activities. In cases
where the bank stabilization activity
affects a special aquatic site, it may be
appropriate for the district engineer to
require compensatory mitigation. For
bank stabilization activities in other
waters of the United States, the district
engineer may determine that it is not
necessary to require compensatory
mitigation.
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Several commenters stated that preconstruction notification should be
required for all activities authorized by
this NWP. One commenter suggested
adding language to clarify that any
requests for waivers of limits for this
NWP would be approved or denied
during the 45-day pre-construction
notification review period. Another
commenter requested that additional
language be added to the text of the
NWP to clarify that bank stabilization
activities are authorized unless
prohibited by the district engineer
following review of the pre-construction
notification.
We do not agree that it is necessary
to require pre-construction notification
for all activities authorized by this
NWP. Many small bank stabilization
activities are conducted each year that
result in minimal adverse effects on the
aquatic environment. We have modified
paragraph (a)(2) of general condition 27
to clarify that NWP activities that
require written waivers of limits are not
authorized unless the district engineer
issues the written waiver. In other
words, a default NWP authorization
does not occur after 45 days if the
proposed activity requires a written
waiver. The modification to general
condition 27 is sufficient to address this
concern, and it is not necessary to
modify the text of this NWP. In the case
of this NWP, all activities that require a
pre-construction notification also
require a written waiver. The Corps will
do its best to process requests for such
waivers within 45 days.
One commenter stated that this NWP
should not be used to authorize bank
stabilization activities in waters of the
United States inhabited by anadromous
fish. One commenter stated that use of
wood in bank stabilization projects may
interfere with tribal rights, such as
treaty fishing access, and therefore
affected tribes should be notified of
requests to use this NWP. Several
commenters said interagency
coordination should be conducted on all
NWP 13 pre-construction notifications.
Division engineers can regionally
condition this NWP to restrict or
prohibit its use in waters inhabited by
anadromous fish. General condition 16,
Tribal Rights, states that activities
authorized by NWP cannot impair
reserved treaty rights. Division and
district engineers should consult with
Tribes to develop regional conditions
where necessary to ensure that tribal
rights are adequately protected by this
NWP. Division engineers can regionally
condition this NWP to require
coordination with Tribes when
proposed NWP activities may affect
Tribal lands or trust resources. General
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condition 27, Pre-Construction
Notification, sets out the requirements
and procedures for interagency
coordination for all NWPs; we do not
believe additional requirements are
necessary for this permit.
A number of commenters requested
clarification as to whether the linear and
running foot limits in this NWP are
applicable to the length of the bank or
the length of the stream channel.
Several commenters stated that the
prohibition against stream
channelization should be retained,
while others recommended that it be
removed because many bank
stabilization activities could be
considered stream channelization
projects. One commenter stated that this
NWP should not be used to authorize
hardening of bank surfaces. A number of
commenters also stated NWP 13 should
only authorize vegetative or
bioengineered stabilization methods and
not bank hardening methods. One
commenter recommended modifying
this NWP to encourage bioengineered
methods, or placement of riprap above
the ordinary high water mark or high
tide line, by not requiring preconstruction notification for such
activities. Two commenters said that
this NWP should be limited to
bioengineering, living shoreline, or
vegetative bank stabilization techniques,
and that individual permits should be
required for bank stabilization activities
involving the placement of rip-rap and
other hard armoring techniques.
The linear foot and cubic yard limits
apply to the length of the bank. We have
modified paragraph (b) of this NWP to
clarify that the 500 linear foot limit
applies to the length of the bank
stabilization activity, not the length of
the stream segment. We are retaining
paragraph (g), since stream
channelization activities may result in
more than minimal adverse effects on
the aquatic environment. Bank
stabilization activities differ from stream
channelization activities in several
ways. Bank stabilization reduces or
eliminates erosion to prevent the loss of
structures or adjacent property, and
typically only one side of a stream is
stabilized. The location and crosssection shape of the waterway is
generally unaffected except for material
placed along the stabilized bank. Stream
channelization alters the length,
location, and/or cross section shape of
a stream channel. Stream channelization
changes the hydraulic flow
characteristics of the stream, reduces
channel complexity and diversity, and
can include bank stabilization on one or
both banks of the channelized
waterway. Stream channelization
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substantially reduces natural stream
functions, while bank stabilization by
itself does not.
We do not agree that this NWP should
be limited to vegetative or
bioengineering techniques. In many
areas, those techniques will not provide
adequate protection to the bank,
especially in those waters where banks
are subjected to substantial wave
energy, such as coastal shorelines. In
those areas, hard bank stabilization
techniques may be the only feasible
option. The pre-construction
notification requirements in this permit
apply to specific situations not directly
related to the type of bank stabilization
used (e.g., hard or vegetative). We do
not believe that the use of bank
hardening methods, in and of itself,
requires a pre-construction notification,
nor do we believe that pre-construction
notification requirements should be
waived simply because a project that
exceeds the 500 foot or one cubic yard
limit, or that involves discharges into
special aquatic sites, uses vegetative or
bioengineering techniques. However, for
such projects, the use of more
environmentally friendly methods may
well be a factor in the district engineer’s
decision regarding whether or not to
grant the requested waiver.
One commenter suggested that in
order to make the one cubic yard per
running foot limit more practical for
bank construction methods in streams of
significant size, this limit should only
apply to the amount of material placed
from the ordinary high water mark to
the streambed, and not to anything
below or above those planes.
Alternatively, the commenter suggested
that this limit could be adjusted to
increase proportionally with increasing
channel depth at the ordinary high
water mark, so that stream magnitude is
taken into account. One commenter
indicated that the language limiting the
placement of erodible material may
discourage plantings on riprap, since
the soil used for those plantings could
be washed away during high flows. One
commenter said that NWP 13 should not
be used with other permits. Another
commenter suggested that this NWP be
conditioned to prohibit the use of waste
concrete for bank stabilization material,
since it may adversely affect the
environment. One commenter
recommended modifying paragraph (d)
(now designated as paragraph (e)) to
state that the placement of material may
not impair surface water flow into or out
of any water of the United States. In the
September 26, 2006, Federal Register
notice, this paragraph referred only to
wetlands.
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The cubic yard limit for this NWP,
along with the waiver provision, is
adequate to provide flexibility while
protecting the aquatic environment and
ensuring that authorized activities result
in minimal adverse effects. We are
retaining the language in paragraph (a),
to help protect water quality. Bank
stabilization projects involving the
installation of plant materials on riprap
may be authorized by this NWP, but
erodible materials should be properly
stabilized within the riprap or stabilized
by other means. This NWP can be used
with other NWPs to authorize single and
complete projects that result in minimal
individual and cumulative adverse
effects on the aquatic environment,
provided the permittee complies with
general condition 24, Use of Multiple
Nationwide Permits. General condition
6, Suitable Material, addresses the use
of suitable material for discharges of
dredged or fill material into waters of
the United States. This general
condition prohibits the use of materials
that contain toxic pollutants in toxic
amounts. We have modified paragraph
(e) by replacing the word ‘‘wetland’’
with ‘‘water of the United States’’ to
help ensure that surface water flows are
maintained.
This NWP is reissued with the
modifications discussed above.
NWP 14. Linear Transportation
Projects. We proposed to modify this
NWP to limit stream channel
modifications to the minimum
necessary to protect the linear
transportation project and state that the
NWP does not authorize temporary
construction, access, and dewatering
activities necessary to construct the
linear transportation project.
Several commenters supported our
proposal to change the first sentence of
this NWP to refer to ‘‘linear
transportation projects’’ instead of
‘‘linear transportation crossings.’’ One
commenter said that this sentence
should be consistent with the definition
of ‘‘single and complete project.’’
We are retaining the proposed
language in the first sentence of this
NWP. However, in the case of linear
transportation projects, a ‘‘single and
complete project’’ consists of a single
crossing of a water of the United States,
or more than one crossing at the same
location (see the definition of ‘‘single
and complete project’’).
One commenter recommended
reducing the acreage limit to 1⁄3 acre.
One commenter said that this NWP
should not be used in tidal waters.
Another commenter stated there should
be a condition requiring culverts to
allow for unimpeded upstream and
downstream passage of fish as well as
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the passage of substrate and wood
expected to be carried by 100 year flow
events.
We do not agree that it is necessary
to reduce the acreage limit to 1⁄3 acre for
all activities authorized by this NWP.
The 1⁄2 acre limit for losses of non-tidal
waters and the 1⁄3 acre limit for losses
of tidal waters, in addition to the preconstruction notification requirements
and other general conditions, will
ensure that this NWP authorizes linear
transportation projects that result in
minimal adverse effects on the aquatic
environment. General condition 2,
Aquatic Life Movements, states that no
activity may disrupt the necessary life
cycle movements of aquatic species,
including those species that normally
migrate through the area. General
condition 9, Management of Water
Flows, states that, to the maximum
extent practicable, the activity must not
restrict or impede the passage of normal
or high flows, unless the primary
purpose is to impound water.
A large number of commenters
objecting to the removal of the language
regarding authorization of temporary
construction, access, and dewatering
activities necessary to construct the
linear transportation project, because
NWP 33 requires pre-construction
notification for all activities. One
commenter suggested that the Corps
expressly state that all activities
authorized previously under this NWP
remain authorized.
We have decided not to remove the
language authorizing the temporary
construction, access, and dewatering
activities from this NWP. In addition,
we have added a new paragraph to this
NWP to help ensure that temporary
impacts associated with NWP 14
activities are minimized, and that
temporary fills are removed and affected
areas are returned to pre-construction
elevations and revegetated as
appropriate.
One commenter said that this NWP
should not authorize the construction of
new transportation or spur projects,
because potential future development
activities might occur after the
transportation project is constructed.
One commenter stated that the NWP
should be applicable only to the
expansion, modification or
improvement of existing linear
transportation projects. One commenter
recommended modifying the preconstruction notification thresholds to
clarify whether temporary losses require
pre-construction notification.
This NWP authorizes the
construction, expansion, modification,
or improvement of linear transportation
projects that result in minimal
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individual and cumulative adverse
effects on the aquatic environment. It
does not prohibit new projects simply
because there may be future
development activities. It would be
impractical to condition use of this
NWP on consideration of hypothetical
effects of potential future activities.
Such effects will be addressed through
applicable permitting requirements if
and when future activities are proposed.
The acreage-based pre-construction
notification threshold applies only to
permanent losses of waters of the
United States. However, preconstruction notification is also
required for any discharges of dredged
or fill material into special aquatic sites,
whether those discharges are permanent
or temporary.
One commenter stated that this NWP
should not authorize bridge footings,
because they result in a significant
impact to stream habitat and that edge
habitat is lost to hardened banks. One
commenter asked whether this NWP
authorizes cul-de-sacs and hammerhead
turnarounds.
Bridge footings are necessary to
construct certain types of linear
transportation projects, and they usually
result in minimal adverse effects on the
aquatic environment. The preconstruction notification thresholds for
this NWP will ensure that district
engineers will review those activities
with bridge footings that have the
potential to result in more than minimal
adverse effects on the aquatic
environment. Bridge footings are
generally confined to narrow stream
segments, so only small amounts of edge
habitat will be lost as a result of the
construction of a bridge footing. In
addition general condition 3, Spawning
Areas, prohibits the physical
destruction of important spawning areas
that could result from these activities.
Discretionary authority will be asserted
in those cases where the construction of
bridge footings will result in more than
minimal individual and cumulative
adverse effects on the aquatic
environment. Cul-de-sacs and
hammerhead turnarounds may be
authorized by this NWP, as they are part
of the street network used for
transportation.
Another commenter recommended
adding storm water management
features to the list of examples of
activities authorized by this NWP. One
commenter requested clarification as to
whether stream modifications,
encroachments, and relocations
associated with highway construction
are authorized. We received several
comments on the proposed language
limiting stream channel modifications
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to the minimum necessary to construct
or protect linear transportation projects.
One commenter objected to the
proposal, stating that it would limit
public transportation safety
requirements by adding unnecessary
restrictions.
Storm water management features are
authorized by this NWP, provided they
are integral features of the linear
transportation project. If they are not,
then they may be authorized by NWP
43, regional general permits, or
individual permits. Stream channel
modifications are authorized by this
NWP provided they are minimized and
conducted in the immediate vicinity of
the project. Otherwise, they require
authorization under another NWP, a
regional general permit, or an individual
permit. This provision allows most
linear transportation projects to use this
NWP while ensuring that they result in
minimal adverse effects on the aquatic
environment.
Two commenters requested further
clarification on the meaning of the
phrase ‘‘minimum necessary.’’ Another
commenter recommended modifying
this NWP to require these activities to
result in no changes to the course or
hydrology of streams.
The phrase ‘‘minimum necessary’’
refers to minimizing the loss of waters
of the United States needed to protect
the project. This is determined based on
case specific circumstances such as the
environmental setting and the nature of
the project. General condition 9,
Management of Water Flows, requires
maintenance of the course, condition,
capacity, and location of open waters,
such as streams, to the maximum extent
practicable. The construction of linear
transportation projects over streams
usually results in some unavoidable
changes to stream morphology, but the
conditions of the NWP authorization
require such impacts to be minimized to
the maximum extent practicable.
Three commenters recommended
adding a 300 linear foot limit to this
NWP, and another commenter suggested
a 2,000 linear foot limit. One commenter
recommended a 200 linear foot limit.
This NWP does not have a linear foot
limit for stream bed impacts. Instead,
the acreage limits for this NWP are
sufficient to ensure that this NWP
authorizes only those activities that
result in minimal individual and
cumulative adverse effects on the
aquatic environment. A 200 linear-foot
limit was previously removed from
NWP 14 to eliminate varied
interpretations and to simplify the basis
for use of the permit.
This NWP is reissued with the
modifications discussed above.
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NWP 15. U.S. Coast Guard Approved
Bridges. There were no changes
proposed for this NWP. One commenter
asked why this permit only applies to
U.S. Coast Guard approved bridges and
not all bridges. The commenter
suggested that the Corps simplify the
permit by revising it to include
construction, repair, seismic retrofit, or
widening of any bridge, regardless of
whether it spans navigable waters.
Another commenter suggested
modifying this NWP to allow the use of
another NWP to authorize the
causeways and approach fills.
The authority to authorize bridges or
causeways across navigable waters of
the United States is held by the U.S.
Coast Guard. This NWP provides
authorization under Section 404 of the
Clean Water Act for discharges of
dredged or fill material into waters of
the United States associated with the
construction of those bridges. The
construction, repair, seismic retrofit, or
widening of these bridges must be
approved by the U.S. Coast Guard. The
environmental review conducted by the
U.S. Coast Guard during its
authorization process will normally
suffice for those related activities that
require the section 404 authorization
provided by this NWP. District
engineers can exercise discretionary
authority when the adverse effects to the
aquatic environment may be more than
minimal. Bridges constructed across
section 404 waters may be authorized by
NWP 14, a regional general permit, or an
individual permit. For the purposes of
clarification, the last sentence of this
NWP is revised to read as follows:
‘‘Causeways and approach fills are not
included in this NWP and will require
a separate Section 404 permit.’’
This NWP is reissued with the
modification discussed above.
NWP 16. Return Water From Upland
Contained Disposal Areas. We proposed
to rearrange the text of this NWP so that
it will be consistent with the format of
the other NWPs. No substantive changes
were proposed to the text of the NWP.
One commenter recommended that the
permit require the issuance of a
National Pollutant Discharge
Elimination System permit under
Section 402 of the Clean Water Act, in
case the return water contains
pollutants entrained in the dredged
material. This commenter expressed
concern that the discharge would not be
properly considered through the water
quality certification process under
Section 401 of the Clean Water Act. One
commenter said that the last sentence
should be modified to acknowledge that
incidental fallback would not require a
section 404 permit.
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Return water from upland contained
disposal areas is administratively
defined as a discharge of dredged or fill
material subject to section 404.
Therefore, section 401 water quality
certification is the appropriate process
for determining whether the discharges
associated with the return water comply
with the appropriate water quality
standards. It is not necessary to qualify
the citation of 33 CFR 323.2(d). District
engineers will use that definition to
determine whether section 404 permits
are required for dredging activities. We
believe that the inclusion of the citation
provides a more complete description of
activities that may constitute a
discharge of dredged material.
The NWP is reissued without change.
NWP 17. Hydropower Projects. We
proposed to rearrange the text of this
NWP, without modifying any of its
terms or its scope. One commenter
stated that the NWP should not apply to
hydropower projects exempt from
Federal Energy Regulatory Commission
licensing requirements. This commenter
remarked that an individual permit
should be required to ensure that
impacts to aquatic resources are
evaluated.
We are retaining the applicability of
this NWP to hydropower projects that
are exempt from the licensing
requirements of the Federal Energy
Regulatory Commission. We believe the
pre-construction notification process
will provide adequate means for district
engineers to assess the impacts to the
aquatic environment and, if necessary,
exercise discretionary authority and
require an individual permit for a
particular activity. In addition, division
and district engineers will condition
such activities where necessary to
ensure that these activities will have no
more than minimal adverse effects on
the aquatic environment, individually
and cumulatively.
The NWP is reissued as proposed.
NWP 18. Minor Discharges. We
proposed to modify this NWP by
applying the 1⁄10 acre limit to all losses
of waters of the United States, not just
special aquatic sites.
Several commenters expressed
support for the proposed revisions. A
few commenters said that this NWP
does not comply with the ‘‘similar in
nature’’ requirement for general permits.
Other commenters asserted that the
cumulative impacts resulting from the
use of this NWP would not be minimal.
Another commenter said that this NWP
should not authorize discharges into
waters inhabited by species of
anadromous salmon.
We believe that the minor scope and
nature of the types of discharge
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activities authorized by this NWP are
sufficient to establish that the activities
are similar in nature. We also maintain
that the discretion vested in district
engineers to issue case-specific special
conditions, including requirements for
appropriate and practicable mitigation,
coupled with the ability of division
engineers to impose regional conditions
for certain activities will ensure
minimal adverse effects on the aquatic
environment, individually and
cumulatively. We disagree that activities
in areas accessible to anadromous
salmonids will necessarily result in
more than minimal impacts. Permittees
must adhere to all applicable NWP
general conditions including general
condition 2, Aquatic Life Movements,
and general condition 3, Spawning
Areas. The terms and conditions of this
NWP, as well as the ability for district
engineers to exercise discretionary
authority, will help ensure that the
activities authorized by this NWP result
in minimal adverse effects to
anadromous salmon.
Several commenters remarked that the
wording of NWP 18 is confusing and
suggested clarifications be provided.
One commenter stated the language
pertaining to ‘‘losses’’ is vague and
suggested we clarify the text by adding
‘‘permanent’’ losses.
We do not agree that additional
modifications are necessary to clarify
the terms and conditions of this NWP.
The proposed revisions to the text of the
NWPs were made to remove redundant
language and simplify the wording to
make it clearer and more concise. The
term ‘‘loss of waters of the United
States’’ is defined in the ‘‘Definitions’’
section which explains that the loss of
waters of the United States includes the
filled area and other waters that are
permanently adversely affected by
flooding, excavation or drainage because
of the regulated activity. Therefore, we
do not agree that elaboration on the term
‘‘losses’’ within the text of this NWP is
warranted.
Some commenters objected to the 1⁄10
acre limit as an unnecessary
administrative burden and unduly
restrictive when coupled with the preconstruction notification requirement.
We do not agree that the 1⁄10 acre limit
will result in an unnecessary
administrative burden or be unduly
restrictive for the regulated public.
While we recognize that the 1⁄10 acre
threshold may preclude use of this NWP
for some activities, we have determined
that activities that result in loss of more
than 1⁄10 acre of waters of the United
States are not necessarily ‘‘minor’’
within the meaning of this permit. We
believe the reduced scope of the permit
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is justified by the enhanced protection
afforded to the aquatic environment and
will better ensure that authorized
activities result in no more that minimal
effects.
Several commenters asserted that a 25
cubic yard threshold is sufficient to
ensure minimal adverse impacts on the
aquatic environment. One commenter
suggested that the volume criteria reflect
a net total volume of discharge or
excavation to allow for the management
of volumes greater than 25 cubic yards
as long as the net total discharged or
excavated does not exceed 25 cubic
yards.
The 25 cubic yard limit for excavating
material, or discharging dredged or fill
material, below the plane of the
ordinary high water mark or high tide
line is necessary to ensure that this
NWP authorizes only those activities
with minimal individual and
cumulative adverse effects on the
aquatic environment. Applying this 25
cubic yard limit to net volumes may
result in more than minimal adverse
effects, because it could allow
substantially larger volumes of material
to be excavated or discharged.
Excavation or discharges of greater than
25 cubic yards in waters of the United
States may be authorized by other types
of permits, including regional general
permits and individual permits. The
language in the September 26, 2006,
proposal also helps simplify the
implementation of this NWP, by
providing clear, easily measured limits
and making it easier to enforce.
Another commenter suggested this
NWP be simplified to authorize only
discharges of dredged or fill material
and exclude excavation activities in
section 10 waters since the Corps does
not regulate excavation activities under
section 404 that result only in incidental
fallback.
Excavation activities may result in
discharges of dredged or fill material
into waters of the United States that
require section 404 permits (see 33 CFR
323.2(d)). Therefore, it is not
appropriate to remove references to
excavation from this NWP. Unless
exempted under Section 404(f) of the
Clean Water Act, excavation activities in
waters of the United States that result in
more than incidental fallback require
section 404 authorization. Minor
discharges authorized under NWP 18
often involve excavation activities that
result in more than incidental fallback
and would therefore constitute a
discharge that is regulated under section
404.
One commenter recommended NWP
18 be specifically prohibited from use
for any new residential and commercial
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construction and that impacts resulting
from new residential or commercial
development be subject to NWPs 29 and
39, respectively.
This NWP authorizes minor
discharges of dredged or fill material in
waters of the United States provided
that the activity complies with the
specific terms and conditions of the
NWP and all applicable NWP general
conditions. The applicability and
verification of the use of this NWP is at
the discretion of district engineers based
on case-specific circumstances.
Therefore, we believe it would be
inappropriate to prohibit its use for new
residential and commercial
development in the absence of casespecific information. We note that the
limits on use of this permit are more
restrictive than the limits on use of
NWPs 29 and 39, so developers could
only use this permit if their impacts
were smaller than those that could be
potentially authorized by these other
NWPs.
One commenter recommended
including language stating that the
discharge will not result in significant
stream geomorphologic or hydrologic
alteration, and that the discharge will
not be placed for the purpose of, or
result in, impeding navigation.
General condition 9, Management of
Water Flows, requires maintenance of
the course, condition, capacity, and
location of open waters, such as
streams, to the maximum extent
practicable. Concerns regarding
potential impacts to navigation are
addressed by general condition 1, which
states that no activity may cause more
than minimal adverse effects on
navigation.
This NWP is reissued as proposed.
NWP 19. Minor Dredging. We
proposed to remove the phrase ‘‘as part
of a single and complete project,’’ since
that requirement applies to all NWPs
and it is not necessary to include that
phrase in the text of this NWP. One
commenter supported the proposed
change.
Another commenter said that the
phrase ‘‘including sites where
submerged aquatic vegetation is
documented to exist but may not be
present in a given year’’ is not
appropriate and recommended that it be
removed. The commenter asserted that
the Corps should not prohibit the use of
this NWP in areas where submerged
aquatic vegetation was present in the
past, but there is no longer evidence that
it is still present.
We are retaining this provision of the
NWP, since areas where submerged
aquatic vegetation is documented to
exist have a high potential for those
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species to return to the area. In a given
year, poor water quality may prevent
submerged aquatic vegetation from
inhabiting that area, but once water
quality improves those plants may grow
back.
One commenter was concerned about
authorizing minor dredging activities in
waters containing habitat features for
various life stages of anadromous fish,
including complex wood structures and
edge habitats used for juvenile rearing
and adult holding. The commenter
indicated that this NWP should not be
used to authorize dredging in waters
that are inhabited by anadromous
salmonids.
The terms and conditions of this
NWP, as well as the ability for division
and district engineers to exercise
discretionary authority or condition this
NWP, are sufficiently protective of
species of anadromous salmon. General
condition 2, Aquatic Life Movements,
specifies no activity may disrupt the
necessary life cycle movements of the
aquatic species indigenous to the
waterbody. In addition, general
condition 3, Spawning Areas, states that
activities in any spawning areas must be
avoided to the maximum extent
practicable during spawning seasons
and the specific terms of this NWP
prohibit its use in anadromous fish
spawning areas at all. Additional time of
year restrictions may be imposed by
division and district engineers to reduce
or avoid impacts to juvenile salmonids
utilizing these areas.
Other commenters expressed
concerns that NWP 19 does not
authorize activities that are similar in
nature with minimal impacts. One
commenter questioned whether this
NWP can be used for removal of a
sandbar across the mouth of a navigable
waterway. A couple of commenters
questioned why this NWP applies to
section 404 waters when the text of the
permit states that it only authorizes
minor dredging activities in section 10
waters. One commenter said that this
NWP should not authorize dredging
activities in non-navigable waters,
including small streams, because of the
greater potential for more than minimal
adverse environmental effects.
We believe that the minor scope and
nature of the types of dredging activities
authorized by this NWP are sufficient to
establish that the activities are similar in
nature. This NWP can only be used to
authorize the removal of materials from
waters subject to Section 10 of the
Rivers and Harbors Act of 1899.
Dredging activities in section 10 waters
may require section 404 authorization,
which may be provided by this NWP. In
waters of the United States that are not
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subject to section 10 jurisdiction (i.e.,
section 404-only waters), NWP 18,
regional general permits, or individual
permits may be used to authorize those
activities. This permit could be used to
remove a sandbar across the mouth of a
Section 10 water provided the activity
met all of the other conditions for its
use.
This NWP is reissued without change.
NWP 20. Oil Spill Cleanup. We did
not propose any substantive changes to
this NWP. One commenter requested
clarification of the applicability of NWP
38 for emergency response to an oil
release in waters of the United States
from electrical equipment that is not
covered by a Spill Prevention, Control,
and Countermeasure (SPCC) Plan. These
releases are governed by EPA’s
polychlorinated biphenyl spill response
regulations at 40 CFR part 761. Because
the activities are not included in a SPCC
Plan, they were not authorized by the
previous or the proposed versions of
NWP 20. Since the required work must
be initiated within 24 or 48 hours of
discovery of the release, the commenter
requested that either NWP 20 be
modified or the pre-construction
notification requirement for NWP 38 be
removed, to allow these activities to
take place in a timely manner.
We agree with the commenter’s
concern but do not think it is
appropriate to remove the preconstruction notification requirement
from NWP 38. We are thus modifying
NWP 20 to authorize the cleanup of oil
releases in waters of the United States
from electrical equipment that are
governed by EPA’s polychlorinated
biphenyl spill response regulations at 40
CFR part 761.
This NWP is reissued with the
modification discussed above.
NWP 21. Surface Coal Mining
Operations. We proposed to change the
title of this NWP. We also proposed
allowing authorization of projects by
this NWP that were currently being
processed as part of an integrated permit
processing procedure in lieu of an
authorization from the Department of
Interior, Office of Surface Mining (OSM)
or by states with approved programs
under Title V of the Surface Mining
Control and Reclamation Act (SMCRA)
of 1977. The Corps, the Environmental
Protection Agency, OSM, and the U.S.
Fish and Wildlife Service entered into a
Memorandum of Understanding on
February 8, 2005. This MOU envisioned
a collaborative process in which the
SMCRA authority chooses to be the lead
agency in coordinating interagency
review of applications for surface coal
mining operations while preserving the
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authorities and responsibilities of each
agency for permit decisions.
We believe there may be some
confusion regarding the intent of the
term ‘‘surface’’ coal mining operations.
The Corps did not intend to restrict use
of this NWP to only a particular type of
coal mining technique. Any coal mining
activities can be considered for
authorization under NWP 21 to the
extent the activities occur on the surface
of the land. In particular, while
discharges associated with underground
coal mining activities now require
authorization under NWP 50 rather than
NWP 21, surface processing activities
associated with underground coal
mining may still be authorized by this
permit provided they meet the
conditions for its use.
Proposed Limits
There were numerous comments
regarding limitations on NWP 21. A
number of commenters recommended
limits on the length of stream that could
be filled under NWP 21, and other
commenters recommended an overall
limit on impacts to waters of the United
States of 1⁄2 acre. One commenter
suggested that the threshold limits
should be 2 acres and 1,500 linear feet.
Three commenters recommended a 300
linear foot limit on filling streams and
a 1⁄2 acre limit on impacts to all waters,
and that these impacts could not be
waived by the district engineer. Two
other commenters concurred with the
300 foot limit but also suggested not
allowing the use of NWP 21 in
watersheds where the cumulative
amount of filled streams was already
causing more than minimal harm.
Several commenters stated that any
linear foot limits should apply to all
streams, ephemeral, intermittent, and
perennial. One commenter said that this
NWP should not authorize discharges
into perennial streams. Another
commenter stated that the use of NWP
21 should not be allowed if more than
10 percent of the headwater streams in
the watershed had been filled or
otherwise degraded. One commenter
stated that a 250-acre watershed limit
was appropriate but that drainage areas
was not the only factor that should be
considered in determining if a project
should qualify for NWP 21.
There were also a substantial number
of comments that objected to limitations
on NWP 21. Many commenters stated
that acreage limits that may be
appropriate for eastern states would not
be appropriate for western states and
would be unnecessarily restrictive. Two
commenters suggested issuing two
versions of NWP 21, one for the western
United States and another for the
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eastern United States. They discussed
the differences in mining and
reclamation techniques and believed the
Corps should recognize these
differences by establishing two NWPs
for coal mining. One commenter noted
that acreage limits need to be larger for
the western United States. A number of
commenters suggested that regional
conditions could be used to address the
issue of limits. Several commenters
noted that there was no compelling
scientific or environmental basis or
rationale to establish limits on NWP 21.
They noted that due to hydrologic,
climatic, and ecological variations, there
was no defensible way to establish a
specific threshold below which impacts
could be said to be ‘‘minimal’’ across
the vastly differing geographical and
hydrological regimes where mining
occurs. Several commenters stated that
arbitrary and unnecessary thresholds
would slow the permit process and
result in a loss of coal production,
which could be construed as a ‘‘takings’’
that violated substantive due process
rights. Other commenters noted that
limiting the use of NWP 21 would result
in a loss in royalty and tax revenues and
increases to the cost of the nation’s
energy supply by restricting coal
production. One commenter noted that
it would take more of the Corps’ limited
resources to review surface mining
projects as individual permits. One
commenter stated that thresholds would
also impact the Corps’ ability to comply
with Executive Order 13212, which
requires federal agencies to expedite
their review of permits for energy
related projects. One commenter noted
that if a 2-acre limit were established for
NWP 21, more than 60 percent of the
nation’s coal production would not be
eligible for the NWP. One commenter
stated that a 3-acre limit in the western
United States would have a significant
impact on Western mining operations.
One commenter noted that if a limit of
less than 50 acres was adopted, the
Corps’ would not achieve its goal of
focusing its limited resources on
projects that have the potential for more
environmentally damaging adverse
effects. Two commenters believed
safeguards were in place to ensure
impacts do not cause more than
minimal individual or cumulative
effects. They noted that general
condition 20, Mitigation, requires
compensatory mitigation to offset the
adverse effects to the aquatic
environment, and that there was no
need for arbitrarily chosen acreage
limits because the mitigation
requirement counterbalances all adverse
effects.
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This NWP is used to provide section
404 authorization for surface coal
mining activities that have also been
authorized by the Office of Surface
Mining or states with approved
programs under Title V of the Surface
Mining Control and Reclamation Act
(SMCRA). Previously, there have been
no limits associated with impacts to
waters of the United States for NWP 21.
This was based partly on the belief that
the analyses and environmental
protection performance standards
required by SMCRA in conjunction with
the pre-construction notification
requirement, are generally sufficient to
ensure that NWP 21 activities result in
minimal individual and cumulative
adverse impacts on the aquatic
environment.
Furthermore, we believe the change in
NWP 21 in 2002, which requires not
only notification to the Corps for all
projects that may be authorized by this
permit but also explicit authorization
from the Corps before the activity can
proceed, has strengthened the
environmental protection for projects
authorized by this permit. One
commenter requested that this
requirement be removed from this NWP.
However, we continue to believe that
this 2002 change helps ensure that no
activity authorized by this permit will
result in greater than minimal adverse
impacts, either individually or
cumulatively, on the aquatic
environment, because it requires a caseby-case review of each project. If the
district engineer determines through
this case-by-case review that the activity
has the potential to result in more than
minimal adverse effects to the aquatic
environment, he or she can exercise
discretionary authority to require an
individual permit. Also, because of the
case-by-case review and the requirement
for written verification, we do not agree
that it is necessary to prohibit
discharges of dredged or fill material
into perennial streams.
Lastly, the Corps recognizes that there
are vast differences in coal mining
techniques not only between the
western and eastern parts of the United
States, but also within the Illinois Coal
Basin and the Appalachian Coal Fields
themselves. There are also considerable
differences in geological, topographical,
climatological, hydrological and
ecological regimes in the areas where
coal resources are located across the
United States. Furthermore, no specific
scientific or environmental basis for
determining a uniform national limit on
NWP 21 was submitted for
consideration. As noted above, there
were several comments suggesting
specific limits but no ecological
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rationale was supplied to support these
specific limits. Several commenters did
submit information from the
Programmatic Environmental Impact
Statement (PEIS) for mountaintop
mining/valley fill. However, the PEIS
did not support or determine
appropriate limits for NWP 21. Based on
these considerations along with the fact
that the impacts to waters vary greatly
depending on the mining techniques
and the environmental factors in the
area, we have determined that
establishing a specific threshold limit
would not be practical on a national
basis. We believe that regional
conditions, as appropriate, and sitespecific review of each pre-construction
notification will ensure that NWP 21
authorizes activities with no more than
minimal adverse effects on the aquatic
environment, individually and
cumulatively. The Corps has
determined that it is both efficient and
environmentally protective to issue an
NWP 21 that can be used to authorize
most activities that have no more than
minimal adverse effects on the aquatic
environment and allow division
engineers to establish regional
conditions that determine appropriate
limits for impacts to waters based on the
functions and values of aquatic
resources within their division.
Regional Conditions
There were three commenters who
noted that the division engineer has the
discretion to add regional terms and
conditions to NWP 21 and that acreage
limitations should be determined at the
regional level. The Corps agrees, based
on the discussion above regarding
limitations, that regional conditions are
the best way to address regional
concerns regarding surface coal mining
activities and NWP 21. Division
engineers can add regional conditions to
any NWP to further restrict the use of
the NWP to ensure that the NWP
authorizes only activities with no more
than minimal adverse effects on the
aquatic environment in a particular
watershed or other geographic region.
The division engineer cannot modify
the NWP by adding regional conditions
to make the NWP less restrictive (see 33
CFR 330.1(d)). The use of regional
conditions recognizes that functions and
values of aquatic resources differ greatly
across the country.
Discretionary Authority
Three commenters noted that NWP 21
allows the Corps to exercise
discretionary authority during the preconstruction notification review process
for any project which has the potential
to cause more than minimal individual
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and cumulative adverse impacts on the
aquatic environment.
We agree with these commenters. The
pre-construction notification
requirements of all NWPs allows for a
case-by-case review of activities that
have the potential to result in more than
minimal adverse effects to the aquatic
environment. If the adverse effects on
the aquatic environment are more than
minimal, then the district engineer can
either add special conditions to the
NWP authorization to ensure that the
activity results in no more than minimal
adverse environmental effects or
exercise discretionary authority to
require an individual permit. While
many NWPs allow the permittee to
assume authorization if he or she has
not heard back from the Corps within 45
days of submitting a complete preconstruction notification, NWP 21
requires written verification before the
project can proceed. This ensures that
adequate time is available to the Corps
to review the extensive documentation
that pre-construction notifications for
NWP 21 often include, coordinate with
other agencies as necessary, and
determine whether exercise of
discretionary authority is necessary to
ensure no more than minimal effects.
Scope of Analysis
One commenter stated that the scope
of analysis for NWP 21 review should
extend beyond the effects of fills in
waters. Another commenter noted that
the Clean Water Act is clear that general
permits may only be issued if the
permitted activities have minimal
impacts on the environment as a whole
and not just the aquatic environment.
Several commenters stated that NWP
21 should not be reissued, in order to
protect wildlife habitat, outdoor
recreation, the quality of life in rural
communities and environmental
integrity. A myriad of comments were
received itemizing impacts related to
authorizations associated with NWP 21.
These impacts included irreversible
damages to the American people, the
destruction of lives and the natural and
cultural heritage of Appalachia,
Montana and Wyoming, loss of hunting
opportunities, the exploitation of
impoverished areas by large
corporations, global warming,
landslides, blasting, truck traffic on
roads not designed or built to handle
heavy loads, harm to bird populations,
destruction of valuable hardwood trees,
loss of medicinal plants, affects on the
tourism/vacation home industry, and
local sickness. Several commenters
stated that mined areas cannot be
restored to pre-mining conditions, such
as native forest. Several commenters
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expressed concern about coal slurry
damaging downstream areas.
All of these impacts are outside of the
Corps’ scope of analysis pursuant to the
National Environmental Policy Act
(NEPA). The Corps evaluation of coal
mining activities is focused on impacts
to aquatic resources. Mining in general
is permitted under a separate Federal
law, the Surface Mining Control and
Reclamation Act. Impacts associated
with surface coal mining and
reclamation operations are
appropriately addressed by the Office of
Surface Mining or the applicable state
agency. Under these circumstances, the
Corps’ NEPA implementing regulations
clearly restrict the Corps’ scope of
analysis to impacts to aquatic resources.
Integrated Permit Process
Several commenters supported the
Memorandum of Understanding (MOU)
between the EPA, Corps, OSM and the
USFWS regarding the integrated permit
process for coal mining mentioned in
the proposed NWP language. Some
suggested the integrated permit process
along with the Standard Operating
Procedure (SOP) for NWP 21 be
mandatory under NWP 21. Some
commenters stated that the integrated
permit process does not eliminate the
dual review of section 404 and SMCRA
as the MOU intended, while other
commenters stated that the integrated
permit process was unlawful because
through it, the Corps has delegated its
section 404 authority to the states
processing the SMCRA permit
applications. One of the commenters
supporting the MOU stated that the
current integrated permit process did
not meet the goal of the MOU, as
evidenced by its failure in Ohio, since
dual reviews were still being
undertaken by the regulatory agencies.
The MOU recommends that Federal
and state agencies coordinate reviews of
coal mining permit applications, with
the SMCRA agency as the lead agency.
Currently, in areas that have developed
or are in the process of developing an
integrated permit process, the agencies
have elected to make the process
voluntary. The integrated permit
process does not eliminate the
regulatory responsibilities of the
participating agencies, but allows the
various permit applications to be
reviewed concurrently while utilizing
information from one application to
fulfill required sections of other
applications, where appropriate. The
process allows for timelier reviews
while providing the framework for
better environmental protection. The
Ohio integrated permit process is still in
use for those who choose to use it.
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State Programmatic General Permits
and Regional General Permits
Several commenters suggested that a
state programmatic or regional general
permit or other methods (e.g., a national
MOU) be developed to reduce the
duplication of effort by the regulatory
agencies, therefore reducing cost and
delays in receiving authorizations.
State programmatic and regional
general permits are developed at the
district level. The Corps supports and
participates in such efforts where
possible.
Surface Mining Control and
Reclamation Act
Several commenters stated that coal
mining is the most environmentally
regulated activity, and SMCRA, along
with Sections 401 and 402 of the Clean
Water Act, already require analyses of
all of the factors addressed under
Section 404 of the Clean Water Act.
Therefore, as the above-referenced
programs already regulate impacts to
aquatic resources, including impacts
related to water quality, endangered
species, historic properties, and the
hydrologic regime, further review by the
Corps only creates an additional
administrative burden without any real
benefits.
The Corps understands coal mining is
covered by many environmental
regulations; however the Corps has
determined that SMCRA, in its current
form, does not remove the need, either
legally or substantively, for independent
authorization under Section 404 of the
Clean Water Act. Consequently, this
NWP does not duplicate the SMCRA
permit process. The Corps continues to
work with the other agencies to avoid
potential duplication of efforts and uses
appropriate work and studies done by or
for other agencies (e.g., surveys/findings
under the Endangered Species Act or
Section 106 of the National Historic
Preservation Act as well as SMCRA
permit documentation) in its analysis of
the proposed project.
Mitigation
Several commenters stated that
mitigation done for NWP 21 is
scientifically indefensible and, absent
such mitigation, the projects authorized
under NWP 21 have more than minimal
adverse effect and are therefore
impermissible. They stated that current
mitigation projects have so far been
unsuccessful and referenced a court
case in the Southern District of West
Virginia (Ohio Valley Environmental
Coalition v. Bulen), where they noted
that a Corps official stated that he did
not know of a single instance of
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successful headwater stream creation.
Also, the commenters stated that the
Corps did not include any specific
guidelines for how to assess stream
function in order to determine the
adequacy of compensatory mitigation.
They also stated that the Corps has not
shown that mitigation will offset the
impacts authorized under NWP 21 or
that off-site enhancement of streams
would fully compensate for functions of
streams that are destroyed. Other
commenters stated that the Corps
mistakenly allows the mitigation
requirements of SMCRA and state water
quality laws to satisfy the independent
requirements of Section 404 of the Clean
Water Act. They stated that allowing a
permittee to claim a compensatory
mitigation or reclamation activity
already required under SMCRA as
compensatory mitigation under the
Clean Water Act is ‘‘double-counting’’
and improperly blurs the requirements
of sequencing (i.e., avoidance,
minimization, mitigation) imposed
under the 404(b)(1) guidelines. Other
commenters recommended that
mitigation of 1:1 should be required in
order to achieve no net loss, and that
mitigation also be required for potential,
as well as actual, impacts. Several
commenters stated that final
reclamation of wetland habitat will most
likely exceed the required compensatory
mitigation.
In order to ensure that an activity
results in no more than minimal adverse
effect on the aquatic environment, the
Corps will add permit conditions that
require compensatory mitigation that
meets specified success criteria. The
Corps will generally require the
permittee to monitor the mitigation site
for five years and, if the mitigation site
does not meet the success criteria at that
time, remediation or additional
mitigation will be required. This
ensures that the authorized activity will
not result in a net loss in aquatic
functions. The Corps has increased its
compliance efforts to ensure that
projects authorized by DA permits are
constructed as authorized and that
mitigation is successful.
We are currently developing new
stream functional assessment protocols
to identify and quantify the functions
lost through authorized impacts and the
functions gained or enhanced through
mitigation. We removed the language
from the proposed NWP 21 that
required the applicant to furnish a
SMCRA or state-approved mitigation
plan. The Corps recognizes that SMCRA
does not require ‘‘mitigation’’ per-se, but
does require ‘‘reclamation/restoration’’,
and that some states require
‘‘mitigation’’ above Corps requirements.
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The Corps coordinates with the SMCRA
and state resource agencies to achieve
appropriate aquatic restoration on mine
sites, which can reduce or eliminate offsite compensatory mitigation needs. The
Corps does not consider this ‘‘doublecounting’’, because the areas restored
are only counted once in the
replacement of aquatic resource
functions. As long as the functions lost
as a result of the permitted activity are
mitigated through the onsite restoration
or enhancement, it does not matter if the
restoration also meets other goals
unrelated to the Section 404 impacts.
General condition 20 establishes the
framework for achieving no net loss of
waters/wetlands, as well as the
sequential review of mitigation on-site.
The Corps takes into account the fact
that, in certain areas and circumstances,
any Corps compensatory mitigation
requirement may be fully encompassed
or exceeded by requirements under
other authorities. As long as the impacts
to the aquatic environment are fully
mitigated, the Corps will not require
additional compensation.
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Withdraw NWP 21
Several commenters requested that
NWP 21 be withdrawn and that the
Corps consider authorizations under
state or regional permits where
cumulative impacts and mitigation
measures can be evaluated on a more
focused level that assures minimal
impacts on the environment.
Division and district engineers have
the authority to revoke or modify any or
all of the NWPs and require
authorizations for proposed projects by
other general permits or individual
permits. This should be determined on
a local level.
Independent Evaluation
Several commenters stated that the
burial or other degradation of hundreds
of miles of Appalachian streams from
mining demands a thorough,
independent review, public notice, and
analysis of alternatives and
minimization, which is provided only
through the individual permit process.
A few commenters stated that coal
mining rearranges the natural landscape
and deserves to be studied on a case-bycase basis. One commenter stated that
each project should be independently
evaluated with proper safeguards in
place to include meaningful bonds that
would be sufficient to cover remediation
costs when companies declare
bankruptcy.
A careful case-specific determination
that a project will result in no more than
minimal impacts is necessary for a
project to be authorized by this NWP.
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The pre-construction notification
process for NWP 21, which requires the
applicant to wait until he or she
receives verification from the Corps,
provides this case-specific
determination. If the District Engineer
determines that a particular proposal
will result in more than minimal
adverse environmental effects, he will
assert discretionary authority and
require an individual permit. Bonding is
covered under general condition 20. The
Corps notes that the SMCRA permitting
process provides for public notice and
comment on all coal mining permits.
Minimal Adverse Effects
A few commenters stated that the
Secretary of the Army can only issue
NWPs by making an up-front
determination that the activities
authorized by each NWP category will
cause only minimal adverse effects and
the Corps cannot ignore harm already
done when assessing cumulative
impacts. The commenters stated that the
Corps has no reasoned basis or
substantial evidence to support its
determinations that the individual or
cumulative environmental impacts
associated with NWP 21 will be
minimal. Several commenters similarly
stated that compensatory mitigation
could not be used to reduce the net
adverse impacts to the minimal level in
order to qualify for general permits.
Therefore, NWP 21 exceeds the
definition of minimal adverse
environmental effects and all coal
mining should be reviewed under the
individual permit process. A number of
commenters stated that surface coal
mining results in significant ecological
damage to headwater stream systems,
when considered both individually and
cumulatively, and it cannot be
reasonably assumed that those stream
losses can be mitigated into
insignificance.
We believe our process for NWP 21
ensures that activities authorized by the
NWP result in no more than minimal
adverse impacts to the aquatic
environment because each project is
reviewed on a case-by-case basis and the
district engineer either makes a minimal
impacts determination on the project or
asserts discretionary authority and
requires an individual permit.
Additionally, as noted above, division
engineers can add regional conditions to
any NWP to further restrict the use of
the NWP to ensure that the NWP
authorizes only activities with no more
than minimal adverse effects on the
aquatic environment in a particular
watershed or other geographic region.
Each district tracks losses of waters of
the United States authorized by
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Department of the Army permits,
including NWPs, as well as
compensatory mitigation achieved
through aquatic resource restoration,
creation, and enhancement.
In addition, we believe that the Corps
can rely on mitigation in making a
minimal adverse environmental effects
determination.
One commenter requested that the
Corps clarify what constitutes a ‘‘single
and complete surface coal mining
operation’’ since approved mines can
expand through either the addition of
substantial acreages or the addition of
small acreages (incidental boundary
revisions). This commenter asked
whether all revisions, including
incidental boundary revisions, are
considered as single and complete coal
mining operations.
District engineers use the criteria in
the definition of ‘‘single and complete
project,’’ which is found in the
‘‘Definitions’’ section of the NWPs,
when identifying single and complete
coal mining operations. District
engineers will determine, on a case-bycase basis, whether the expansion of an
existing mine constitutes a separate
single and complete project.
Impacts From NWP 21 Activities
Many commenters opposed the
reissuance of NWP 21 because of the
potential impacts to the aquatic
environment and water resources.
Several commenters expressed concerns
about impacts to water supplies and
drinking water, downstream water uses,
and recreational opportunities such as
fishing. Concerns were also expressed
about water pollution, the effects of
burying streams that support aquifers,
and loss of streams and wetlands. This
NWP requires compliance with all of
the general conditions for the NWPs,
which address many of these concerns.
Additionally, many of these factors will
be evaluated during the project-specific
evaluation.
One commenter noted that NWP 21
does not provide the public an
opportunity to comment on the specific
conditions of a permit that will affect
their communities and watersheds.
Section 404(e) of the Clean Water Act
provides the statutory authority for the
issuance of general permits on a
nationwide basis for any category of
activities. The Corps establishes NWPs
in accordance with section 404(e), by
publishing and requesting comments on
the proposed permits. The general
public has the opportunity to comment
on NWPs at this time. In order to
address the requirements of the National
Environmental Policy Act, the Corps
prepares a decision document for each
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NWP along with a 404(b)(1) Guidelines
analysis. The decision document
discusses the anticipated impacts on the
Corps’ public interest factors from a
national perspective. NWPs are issued
at the conclusion of this process. The
individual projects that are proposed for
authorization under an NWP are not
given a permit but a verification or
authorization that the project complies
with an NWP. There are no
requirements for public comments on
specific projects authorized under
NWPs. However, in the case of NWP 21,
all projects must have undergone a
separate SMCRA review process the
provides for public notice and
comment.
Several commenters recommended
that NWP 21 be eliminated because it
fails to require that the applicant
demonstrate that there are no
practicable alternatives to placing fill in
waters of the United States, a
requirement of Section 404(e) of the
Clean Water Act. The commenters
stated that the Corps wrongly assumes
the SMCRA process to be comparable to
Section 404 and the 404(b)(1)
Guidelines. The commenters noted that,
in fact, SMCRA does not require the
applicant to choose the method of coal
waste management that avoids and
minimizes impacts and is least
damaging to waters of the United States.
The Corps does not assume that other
state or Federal agencies conduct a
review that is comparable to the section
404(b)(1) Guidelines. Although analysis
of offsite alternatives is not required in
conjunction with general permits, each
proposed project is evaluated for onsite
avoidance and minimization, in
accordance with general condition 20,
and is not authorized under the NWP if
the adverse impacts to waters of the
United States are more than minimal.
Five commenters noted that coal
slurry impoundments should not be
allowed by an NWP and that NWPs can
only be issued for activities that are
similar in nature and that valley fills
and coal slurry impoundments are not
similar in nature.
The Corps has determined that slurry
impoundments and valley fills are part
of surface coal mining activities and are
therefore similar in nature. The ‘‘similar
in nature’’ requirement does not mean
that activities authorized by an NWP
must be identical to each other. We
believe the ‘‘categories of activities that
are similar in nature’’ requirement of
Section 404(e) is to be interpreted
broadly, for practical implementation of
the NWP program.
The NWP is reissued as proposed.
NWP 22. Removal of Vessels. We
proposed to rearrange the text of this
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NWP so that it is in a format similar to
the other NWPs. In addition, we
proposed to require pre-construction
notification if the activity requires
discharges of dredged or fill material
into special aquatic sites.
One commenter asked if the preconstruction notification requirement
included marine protected areas. One
commenter said that pre-construction
notification should be required for all
vessel removals because certain removal
methodologies may result in additional
environmental impacts. One commenter
stated that pre-construction notification
should be required for all vessel
removals from special aquatic sites, not
just those involving discharges of
dredged or fill material.
Pre-construction notification is
required for NWP 22 activities in
designated critical resources waters and
their adjacent wetlands (see general
condition 19), which may include
marine protected areas. Designated
critical resource waters include NOAAdesignated marine sanctuaries, Natural
Estuarine Research Reserves, and other
waters identified by the district engineer
after the issuance of a public notice and
an opportunity for public comment. We
do not agree that pre-construction
notification should be required for all
activities authorized by this NWP.
However, we are modifying this NWP to
require pre-construction notification for
activities in special aquatic sites, to
ensure that those activities result in
minimal adverse effects on the aquatic
environment. Vessel removal activities
in special aquatic sites, especially coral
reefs and vegetated shallows, have the
potential to result in more than minimal
adverse effects, even though there may
be no discharge of dredged or fill
material. Vessel removal activities in
other areas conducted in compliance
with the NWP and the general
conditions will normally have no more
than minimal adverse effects on the
aquatic environment, individually and
cumulatively. Further, division and
district engineers will condition these
activities as necessary to ensure that
they will have no more than minimal
adverse effects on the aquatic
environment, individually and
cumulatively.
Another commenter observed that
vehicles are often found in waters of the
United States due to accidents,
abandonment, and other reasons, and
that the removal of the vehicles is
necessary to minimize the adverse
environmental impacts associated with
release of automotive fluids. The
commenter requested that this NWP be
modified to allow for the expedited
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removal of vehicles from waters of the
United States.
We agree that the presence of
vehicles, and the associated automotive
fluids, in waters of the United States can
be environmentally damaging, and this
NWP can be used to authorize their
removal when they constitute an
obstruction to navigation. However, we
believe that the pre-construction
notification requirements for activities
into special aquatic sites are necessary
to ensure that the activities authorized
by this NWP have no more than
minimal adverse effects. Division and
district engineers can evaluate projects
on a case by basis in situations where
pollutants may be leaking from vehicles
and determine if expedited or
emergency processing procedures are
warranted.
A commenter requested that the Corps
indicate when EPA and Corps permits
are required or provide citations to EPA
and Corps regulations. One commenter
noted that the parenthetical
identification of statutory authorities
was not included at the end of the text
for this NWP.
The ‘‘Note’’ to this NWP already
includes a citation of applicable EPA
regulations. We do not believe it is
necessary to add citations to the Corps
regulations for implementing Section
404 of the Clean Water Act and Section
10 of the Rivers and Harbors Act of
1899. We are correcting this NWP to
identify the statutory authorities under
which this NWP is issued (i.e., sections
10 and 404).
Another commenter requested that
the Corps clarify in the preamble to the
final rule that this NWP also applies to
the removal of objects and structures
such as derelict mooring and breasting
structures, piles, docks, bridges and
trestles that are man made obstructions
to navigation. They remarked that some
districts apply this NWP only to the
removal of vessels. One commenter
requested clarification as to when a preconstruction notification is required
with respect to general condition 18,
Historic Properties. They asked if the
permittee would have to wait to remove
the vessel until after the district
engineer has informed the permittee
that compliance with general condition
18 is complete.
The text of the NWP clearly states that
the NWP applies to the removal of manmade obstructions to navigation, which
may include any of the obstructions
identified by the commenter in addition
to wrecked, abandoned, or disabled
vessels. If the vessel is listed, or eligible
for listing, in the National Register of
Historic Places, then consultation under
Section 106 of the National Historic
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Preservation Act is required. The
permittee would have to wait until the
section 106 process has been completed
before conducting the work.
The NWP is reissued with the
modification discussed above.
NWP 23. Approved Categorical
Exclusions. We proposed to modify this
NWP by reorganizing the text, adding
language to explain that Corps’
Regulatory Guidance Letters (RGLs) list
the approved Categorical Exclusion (CE)
activities, and adding language that
directs prospective permittees to the
appropriate RGLs to determine if preconstruction notification is required.
One commenter supported the
proposed rewording of NWP 23, and
supported the clarification of preconstruction notification requirements.
One commenter remarked that this NWP
violates the intent of the National
Environmental Policy Act (NEPA) by
enabling developers to avoid addressing
ecological impacts.
The process for approving categorical
exclusions for use with this NWP,
including any approved categorical
exclusions that require pre-construction
notification, helps ensure that this NWP
authorizes only those activities that
result in minimal individual and
cumulative adverse effects on the
aquatic environment and the public
interest. In addition, only the actions of
government agencies qualify for this
NWP.
Another commenter suggested
requiring pre-construction notification
for activities adversely affecting more
than 1⁄10 acre of wetland, and
recommended adding a 1⁄3-acre limit to
this NWP for wetland impacts. One
commenter suggested that larger
activities should be evaluated under
individual permit procedures instead of
using this NWP, and suggested that
large highway projects impacting
wetlands should not be authorized
without the public involvement and the
environmental safeguards of the
404(b)(1) Guidelines. One commenter
suggested that all projects requiring
stream channelization and any bridges
spanning less than 1.5 times the
bankfull width of a stream should be
evaluated through the individual permit
process.
The pre-construction notification
thresholds established for the
categorical exclusions approved for use
with this NWP require case-by-case
review for activities that have the
potential to result in more than minimal
adverse effects on the aquatic
environment. For the same reasons, it is
not necessary to impose an acreage limit
on this NWP or require individual
permits for large highway projects that
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impact small amounts of waters of the
United States and qualify for approved
categorical exclusions. In response to a
pre-construction notification, the
district engineer can add special
conditions to the NWP authorization to
ensure that adverse effects on the
aquatic environment are minimal or
exercise discretionary authority to
require an individual permit for the
work.
Two commenters said that this NWP
authorizes activities that are not similar
in nature. One commenter suggested
that categorizing impacts by the effects
instead of by the nature of activity is
invalid, and that there appeared to be no
limiting principle on the nature of the
activities that could be permitted.
Regulatory Guidance Letter 05–07
lists all categorical exclusions currently
approved for use with this NWP as of
the date of this notice. This RGL is
available on the Internet at: https://
www.usace.army.mil/cw/cecwo/reg/rgls/
rgl_05_07_v2.pdf. The lists of approved
categorical exclusion activities
referenced in RGL 05–07 represents
impacts that are minor in nature, both
individually and collectively. A limiting
principle on the nature of activities
exists because each government agency
has inherent and mission-specific
responsibilities and projects, and
activities proposed by a specific agency
within an approved categorical
exclusion are similar in nature. The
primary Federal action agency
determines that the activities are
categorically excluded from further
environmental review. We believe that
normally these activities will have no
more than minimal adverse effects on
the aquatic environment, individually
and cumulatively. However, division
and district engineers can condition
such activities where necessary to
ensure there will be no more than
minimal adverse effects on the aquatic
environment, or exercise discretionary
authority to require an individual
permit for the work.
Two commenters asserted that the
NWP fails to comply with a statutory
requirement that the activities have
minimal impacts individually and
cumulatively. One of these commenters
said that the Corps’ estimate of 1,020
acres of impact to waters of the United
States represents a significant impact.
We disagree with this assertion. Preconstruction notification is required for
certain approved categorical exclusions
that apply to activities that have the
potential to result in more than minimal
individual and cumulative adverse
effects on the aquatic environment. In
general, impacts authorized by this
NWP are not significant because they
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are individually minor, are widely
distributed across a vast area, and are
scattered across many watersheds. In
addition, compensatory mitigation
offsets the authorized losses, and helps
ensure that the authorized activities
result in minimal adverse effects on the
aquatic environment.
One commenter objected to the lack of
specificity regarding the method of
solicitation of public comments if new
categorically excluded activities are
proposed.
When proposing to add categorical
exclusions for use with this NWP, Corps
Headquarters publishes a proposal in
the ‘‘Notices’’ section of the Federal
Register. Public comment will be
solicited through this notice, and all
comments received will be thoroughly
considered when the Corps makes its
determination regarding those proposed
categorical exclusions.
One commenter asked that the ‘‘Note’’
at the end of this NWP be expanded to
list all of the agencies or departments
that have categorical exclusions
approved for use under this NWP. One
commenter believed that referencing
RGLs in the NWP is not sufficient, and
suggested that the list of approved
activities and pre-construction
notification requirements be wholly
included within the text of the permit
rather than referenced to a separate
document. Another commenter stated
that the pre-construction notification
requirements are vague, and
recommended stating the preconstruction notification requirements
within the text of the NWP or listing the
specific RGL to refer to for those preconstruction notification requirements.
We have modified the ‘‘Note’’ by
adding a sentence listing the agencies
with approved categorical exclusions.
Listing the approved activities and preconstruction notification requirements
in the text of the permit is impractical,
because of the lengths of those lists. In
addition, simply referencing the list of
RGLs is more useful because additional
RGLs may be issued if more categorical
exclusions are approved for use with
this NWP.
One commenter asked that the text of
this NWP be amended to acknowledge
that state transportation agencies can
legally assume the responsibility for
categorical exclusion determinations for
the Federal Highway Administration
(FHWA).
The current text of the NWP states
that activities ‘‘undertaken, assisted,
authorized, regulated, funded, or
financed’’ in whole or in part by a
Federal agency are eligible to be
considered by the Corps for possible
approval as a categorical exclusion. We
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believe that the current text is sufficient
and there is no need to restate or affirm
the relationships between the FHWA
and the state transportation agencies,
which generally fall into one or more of
these categories.
This NWP is reissued as proposed.
NWP 24. Indian Tribe or State
Administered Section 404 Programs. We
proposed to add Indian tribes to this
NWP, since they can be approved by
EPA to administer the section 404
program. No comments were received.
This NWP is reissued as proposed.
NWP 25. Structural Discharges. No
changes to this NWP were proposed.
One commenter stated that it is difficult
to perform these types of activities
without some minor related temporary
construction activity. They suggest
adding a statement that allows minor
construction activities.
The construction of these structural
members is usually accomplished by
installing sheeting or pilings to
construct forms, which are then filled
with concrete, sand, rock, or other
materials. The installation of the
sheeting or pilings usually does not
result in a discharge of fill material that
would require section 404
authorization. However, in cases where
temporary construction, access, and
dewatering activities are necessary to
complete the activities authorized by
this NWP, those temporary activities
may be authorized by NWP 33, a
regional general permit, or an individual
permit.
The NWP is reissued as proposed.
NWP 27. Aquatic Habitat Restoration,
Establishment, and Enhancement
Activities. We proposed to modify this
NWP by requiring reporting to the
district engineer for those activities that
do not require pre-construction
notification. We also proposed to add
shellfish seeding to the list of examples
of activities authorized by this NWP,
and remove the restriction limiting the
use of this NWP only to those mitigation
banks that have been approved in
accordance with the 1995 mitigation
banking guidelines. In addition, we
proposed to prohibit the use of the NWP
to authorize the conversion of natural
wetlands.
We have modified the first paragraph
of this NWP to more clearly present the
general categories of authorized
activities.
One commenter supported the
broadening of the title of this NWP to
include all aquatic habitats. One
commenter said that this NWP has the
potential to authorize projects with
significant adverse impacts. One
commenter said that this NWP should
be revoked, because it could result in
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losses of wetland function and habitat
and other adverse impacts to the aquatic
environment. One commenter stated
that there should be an acreage limit on
this NWP. Two commenters said that
wetland impacts should be limited to 2
acres, and another commenter stated
that stream impacts should be limited to
2,000 linear feet. Another commenter
stated that the lack of an acreage limit
on this NWP does not encourage
applicants to minimize adverse impacts.
This commenter suggested a 1⁄2 acre
limit for wetland fills and a 300 linear
foot limit for stream impacts.
This NWP authorizes aquatic habitat
restoration, establishment, and
enhancement activities, provided those
activities result in net increases in
aquatic resource functions and services.
Its use will not cause significant adverse
effects on the overall aquatic
environment. We do not believe there
should be an acreage limit on this NWP,
because of the requirement for these
projects to result in net increases in
aquatic resource functions and services.
Moreover, all activities authorized
under this NWP will be reviewed in
advance by the Corps, either through the
pre-construction notification
requirement, or through the reporting
requirement for projects conducted
under authorities of other Federal
agencies.
One commenter recommended
prohibiting establishment of open water
areas in existing wetlands and streams,
and prohibiting the relocation of all
aquatic resources. One commenter
recommended removing the references
to waterfowl impoundments because
those impoundments may be considered
enhancements by some people. This
commenter said the establishment of
impoundments in streams or natural
wetlands should not be allowed for any
reason. One commenter requested
clarification whether this NWP
authorizes green-tree reservoirs. One
commenter suggested allowing dam
removal activities to be authorized by
this NWP. One commenter said that this
NWP should authorize stream
establishment, in cases where impaired
or degraded streams can be relocated to
provide net benefits to the aquatic
environment and the overall watershed.
We have modified the text of this
NWP, by removing the reference to
establishing an impoundment for
wildlife habitat. This NWP does not
authorize green-tree reservoirs, because
those activities generally degrade
natural wetlands and would not result
in a net increase in aquatic resource
functions and services. Discharges of
dredged or fill material into waters of
the United States for the continued
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operation of existing green-tree
reservoirs may be authorized by NWP
30. New green-tree reservoirs may be
authorized by individual permits or
regional general permits. This NWP
prohibits the conversion of streams or
natural wetlands to other aquatic habitat
types or uplands, except for the
relocation of non-tidal waters on the
project site. We have also simplified the
language regarding the relocation of
non-tidal waters, including non-tidal
wetlands, on the project site. The
requirement that such relocations
provide net gains in aquatic resource
functions and services has been
retained. Dam removal activities can be
authorized by this NWP, provided they
meet the requirements for its use,
including that there is a net increase in
aquatic resource functions and services.
We have modified the third paragraph
of this NWP to state that this NWP can
be used to authorize the relocation of
non-tidal streams, provided there are
net increases to aquatic resource
functions and services.
One commenter stated that using this
NWP to authorize the relocation of nontidal waters, including non-tidal
wetlands, on the project site as long as
there are net gains in aquatic resource
functions and services, appears to
contradict the provision prohibiting the
conversion of streams or natural
wetlands to another aquatic use. This
commenter indicated that there will be
different interpretations of the relative
value of certain aquatic resource
functions and services. This commenter
also said that temporal lags associated
with replacing certain wetland types,
such as forested wetlands, should be
considered.
The relocation of non-tidal waters on
a project site does not necessarily
contradict the provision prohibiting the
conversion of streams or natural
wetlands to another aquatic habitat
type, if comparable streams or wetlands
are restored or established elsewhere on
the project site. District engineers will
determine compliance with these
provisions on a case-by-case basis, in
response to a pre-construction
notification or a report. We recognize
that relocating non-tidal waters may
result in temporal losses of certain
aquatic resource functions and services,
while the relocated waters undergo
ecosystem development. To comply
with these provisions of this NWP, the
net increases in aquatic resource
functions and services does not need to
occur immediately after the NWP 27
activity has been constructed. However,
those net increases need to occur over
time through ecosystem development
processes as a result of a successful
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aquatic habitat restoration,
establishment, or enhancement activity.
Two commenters noted that
conversion of streams or wetlands to
other aquatic uses is prohibited but
conversions of waters to uplands are not
prohibited. Three commenters
supported the proposed language
prohibiting conversion of streams or
natural wetlands to other aquatic uses.
Another commenter supported the
language prohibiting conversion of
wetlands to other aquatic uses, but said
that it may limit the usefulness of this
NWP, as it will not be able to authorize
large ecosystem restoration projects that
involve conversions of wetlands to other
aquatic types, even where there are net
benefits for the aquatic environment.
We have modified this NWP to
prohibit the conversion of streams or
natural wetlands to uplands. This
prohibition does not apply to projects
involving the relocation of non-tidal
waters on the project site, as long as
those activities result in net increases in
aquatic resource functions and services.
Large ecosystem restoration projects that
involve conversions of aquatic habitat to
other aquatic uses are more
appropriately authorized through either
regional general permits or individual
permits.
To prevent re-arrangement of
wetlands within a single development
tract, one commenter asked that this
NWP prohibit the relocation of aquatic
habitat types on parcels where a local
planning document exists for the
development. One commenter objected
to prohibiting the conversion of natural
wetlands to other aquatic uses on the
grounds that NWPs are intended to
allow any activities with minimal
adverse effects. This commenter stated
that some conversions enhance
ecosystem functions.
This NWP can be used to authorize
relocation of aquatic habitats on a
project site, even those with
development activities, provided there
are net gains in aquatic resource
functions and services. These activities
can be beneficial in cases where the
development activity could have
indirect adverse effects on the functions
of existing aquatic resources on the
project site, and where relocating those
aquatic resources would result in
enhanced ecosystem functions. We have
revised the text of this NWP to prohibit
the conversion of natural wetlands to
other uses, unless that conversion is
part of relocating non-tidal waters on
the project site. This NWP does not
authorize stream channelization, which
often involves extensive armoring and
straightening of stream channels.
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One commenter suggested allowing
the use of NWP 27 for the restoration
and enhancement of tidal streams and
tidal open waters. Another commenter
said that this NWP should authorize the
relocation and/or conversion of any
tidal waters, provided the proposed
work would result in net increases in
aquatic resource functions and services.
One commenter stated that this NWP
should not authorize the construction of
impoundments or partial
impoundments in tidal wetlands or
estuarine waters.
This NWP does not authorize the
restoration of tidal streams and tidal
open waters, but may authorize the
restoration of riparian areas next to such
waters. The restoration of tidal streams
and other tidal open waters that involve
more than restoring riparian areas is
more appropriately authorized by other
Department of the Army permits, since
those activities may result in more than
minimal adverse effects on the aquatic
environment. We do not believe it
would be appropriate to modify this
NWP to authorize those activities. We
maintain our position that this NWP
should not authorize the relocation or
conversion of tidal waters. Those
activities may be authorized by
individual permits or regional general
permits. This NWP does not authorize
the conversion of tidal waters to other
uses, such as impoundments or partial
impoundments.
One commenter said that many
activities proposed as restoration
actually degrade habitat or result in a
net loss of habitat, and stated that preconstruction notification should be
required for all activities authorized by
this NWP, to determine the beneficial
effects and whether the activity is
protective of tribal resources.
Pre-construction notification is
required for activities authorized by this
NWP, except for those activities
conducted in accordance with binding
agreements between certain Federal
agencies or their designated state
cooperating agencies, voluntary wetland
activities documented by the NRCS or
USDA Technical Service Provider
pursuant to NRCS Field Office
Technical Guide standards, or the
reclamation of surface coal mining
lands, in accordance with permits
issued by the Office of Surface Mining
or the applicable state agency. For those
activities that do not require preconstruction notification, reporting to
the district engineer is required. In the
latter cases, the district engineer can
review the documentation provided
through reporting to ensure that the
activity qualifies for NWP authorization.
The reporting requirements provide
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district engineers with the opportunity
to review aquatic habitat restoration,
establishment, and enhancement
activities conducted under the purview
of other government entities, to ensure
that those activities result in net
increases in aquatic resource functions
and services. The pre-construction
notification requirements, as well as the
reporting requirements, will help ensure
that this NWP authorizes only activities
that comply with the terms and
conditions of this NWP, including
general condition 16, Tribal Rights.
One commenter stated that the
reporting requirement for voluntary
NRCS-related wetland projects would be
burdensome, and suggested that
requiring NRCS documentation could
discourage voluntary wetland
restoration activities. Another
commenter said that there appears to be
little difference between the reporting
and pre-construction notification
provisions, and suggested requiring preconstruction notifications for all NWP
27 activities. Two commenters
supported the requirement that copies
of restoration agreements be submitted.
One commenter recommended requiring
pre-construction notifications and
interagency coordination for all projects
using NWP 27, to ensure that
development activities are not
conducted as NWP 27 activities. A
commenter objected to requiring the
submittal of restoration agreements to
fulfill the reporting requirement, citing
privacy concerns. This commenter said
that alternative types of information
could be submitted instead to report
proposed NWP 27 activities conducted
under these agreements. One
commenter stated that the Corps and
other agencies should be required to
approve wetland enhancement,
restoration, or establishment agreements
referenced in the reversion provisions of
NWP 27.
The pre-construction notification
requirements are sufficient to ensure
proper implementation of NWP 27. We
have clarified the language in the NWP
to reduce confusion. To avoid
duplicative efforts by the government,
pre-construction notification is not
required for activities conducted under
agreements or arrangements with other
state or Federal government agencies.
Pre-construction notification is required
for all other activities. The reporting
requirement will provide a mechanism
whereby the Corps can review proposed
activities conducted under other agency
programs, to ensure that they comply
with the terms and conditions of this
NWP. We are modifying the reporting
requirement to allow the submittal of
project descriptions and plans, in lieu of
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binding agreements executed between
agencies and landowners.
It would be inappropriate to require
Corps approval of wetland
enhancement, restoration, or
establishment agreements executed and
administered by other agencies. For
those activities that require preconstruction notification and will result
in the loss of greater than 1⁄2 acre of
waters of the United States, agency
coordination is required (see paragraph
(d) of general condition 27).
One commenter suggested modifying
the reversion, reporting, and notification
provisions by referencing actions
documented by ‘‘NRCS or USDA
Technical Service Provider pursuant to
NRCS Field Office Technical Guide
Standards’’ instead of ‘‘NRCS
regulations,’’ since many of these
wetland restoration, enhancement, and
establishment activities are performed
by technical service providers, who
must be certified by NRCS and comply
with the Field Office Technical Guide
standards. We concur with this
recommendation, and have made
appropriate changes to the text of this
NWP.
One commenter said that replacing
the word ‘‘values’’ with ‘‘services’’
demeans the functions provided by a
healthy ecosystem, unless the term
‘‘functions’’ is specifically retained.
Another commenter remarked that
replacing the word ‘‘values’’ with
‘‘services’’ is inconsistent with the
common industry vernacular. They
suggest using the word ‘‘functions’’
instead of ‘‘services.’’
We are retaining the term ‘‘functions’’
in the text of this NWP, and are
replacing the word ‘‘values’’ with
‘‘services’’ because ecosystem services
provide a more objective measure of the
importance of aquatic resource
functions to human populations. The
terms ‘‘functions’’ and ‘‘services’’ are
not equivalent, and therefore it would
not be appropriate to replace the term
‘‘services’’ with ‘‘functions.’’ Services
are the benefits that humans derive from
the functions performed by wetlands
and other aquatic resources. The term
‘‘services’’ is now being used in place of
‘‘values’’ in the ecological economics
literature, because of the difficulty in
assigning value to ecosystem services.
As discussed in the September 26, 2006,
Federal Register notice, values may
relate to either monetary or nonmonetary measures, but services can be
described in physical terms that are
easier to evaluate and address, where
necessary, in NWP authorization letters
and special permit conditions.
Two commenters supported allowing
the use of NWP 27 to authorize the
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construction of mitigation banks. One
commenter requested clarification that
this NWP could be used for wetland
mitigation banks, and one commenter
asked that the NWP apply to all
mitigation banking projects, not just
those with a signed mitigation banking
agreement. Two commenters said that
the construction of mitigation banks
should not be authorized by NWP 27,
but should be authorized by individual
permits instead. One commenter stated
that it would be acceptable to allow the
use of NWP 27 for mitigation bank
construction with a caveat that impacts
associated with mitigation bank
construction be deducted from any
available credit the mitigation bank
develops. One commenter requested
that this NWP contain language stating
that compensatory mitigation is
required for activities authorized by
NWP 27, but another commenter
suggested that no compensatory
mitigation should be required for
impacts associated with construction of
compensatory mitigation projects.
This NWP can be used to authorize
aquatic resource restoration,
establishment, and enhancement
activities necessary for the construction
of mitigation banks. It is not necessary
for the mitigation bank proponent to
obtain a signed mitigation banking
instrument prior to conducting the NWP
27 activity, but the mitigation bank
proponent needs to understand that
activities conducted prior to approval of
a banking instrument may or may not be
approved in any final instrument. The
Corps thus recommends that
construction of mitigation banks not
begin until a final instrument has been
signed. Requiring compensatory
mitigation for losses of waters of the
United States as a result of NWP 27 is
at the discretion of the district engineer.
The crediting of a mitigation bank will
be determined by the district engineer
during the approval process for the
mitigation banking instrument. Any
adverse impacts to aquatic resources
resulting from construction of the bank
would certainly be considered in that
determination.
Two commenters said that this NWP
should require permittees to plant
native species at the site. They said that
the proposed language contains too
much flexibility. One commenter said
that NWP 27 should not authorize
activities in waters inhabited by
anadromous fish. One commenter stated
that the U.S. Fish and Wildlife Service
must concur with projects in which
machinery must work in waters where
endangered or threatened species are
present. One commenter indicated that
this NWP should authorize work in
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flowing waters where the activity will
result in long-term stability and habitat
benefits.
It would be inappropriate to require
permittees to plant only native species
at the project site. Native plant materials
may not be available for all of these
projects, and it is difficult to define
precisely what constitutes a ‘‘native’’
species. The activities authorized by
this NWP are required to result in net
increases in aquatic resource functions
and services, which should benefit
anadromous fish species. However,
district engineers will review preconstruction notifications and other
reported activities to determine if the
proposed aquatic habitat restoration,
establishment, or enhancement activity
would have more than minimal adverse
effects on anadromous fish species, or
require consultation under Section 7 of
the Endangered Species Act. In
addition, division and district engineers
can develop regional conditions or casespecific conditions to ensure that
potential impacts to anadromous fish
are minimal, or exercise discretionary
authority to require an individual
permit for the work if impacts are
expected to be more than minimal.
Compliance with the other general
conditions for the NWPs, including
general condition 9, Management of
Water Flows, is required, though general
condition 9 specifically allows activities
that alter the pre-construction course,
condition, capacity, and location of
open waters if they benefit the aquatic
environment.
One commenter requested
clarification of what constitutes a
‘‘small’’ nesting island, and requested
that the NWP state that approved water
quality standards cannot be violated
during construction of small nesting
islands. Another commenter said that
pre-construction notification should be
required for the construction of small
nesting islands in special aquatic sites.
One commenter asked for a definition of
the term ‘‘enhancement activities.’’ One
commenter suggested requiring
monitoring of stream restoration
projects, with mandatory corrective
actions for projects that are not
successful.
The district engineer has the
discretion to determine what a ‘‘small
nesting island’’ is for the purposes of
this NWP. Either pre-construction
notification or reporting is required for
all activities authorized by this NWP,
which will provide district engineers
with opportunities to review all
proposed activities, including the
construction of small nesting islands, to
determine those activities comply with
the terms and conditions of the NWP.
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The term ‘‘enhancement’’ is defined in
the ‘‘Definitions’’ section of the NWPs.
District engineers have the authority to
require additional monitoring or
corrective measures on a case-specific
basis. We believe it is unnecessary to
restate those authorities in the text of
this NWP.
One commenter said that this NWP
should prohibit the widening or
straightening of stream channels, the
removal of gravel bars, the destruction
of woody vegetation, and the in-stream
use of bulldozing or heavy equipment.
Another commenter stated that NWP 27
should require the use of natural stream
channel design for in-stream work. Two
commenters suggested that this NWP
should not authorize the use of riprap
or other armoring. One commenter
suggested limiting the use of this NWP
to restoration of a stream to its historic
non-degraded condition to prevent the
use of this NWP for construction of
flood control projects.
This NWP does not authorize stream
channelization activities. It may be
necessary to temporarily impact gravel
bars or vegetation during the
construction of stream restoration and
enhancement activities. After the
construction of the stream restoration or
enhancement project, the stream
channel should move water and
sediment in a manner that will result in
a channel morphology that provides
habitat for a diverse community of
species. That restored or enhanced
habitat will include gravel bars, if the
bed load carried by the stream includes
a sufficient proportion of gravel. In
addition riparian vegetation will
normally be planted or allowed to grow
back to replace the impacted riparian
vegetation after construction activities
have been completed. In-stream use of
heavy equipment is not prohibited,
because such equipment is usually
necessary to conduct stream restoration
and enhancement activities. In response
to a pre-construction notification, or the
review of the other Federal agency
agreement, the district engineer will
determine whether the proposed
activity complies with the terms and
conditions of the NWP, including the
requirement for the activity to result in
net increases in aquatic resource
functions and services. It would be
inappropriate to require, in the text of
this NWP, specific design or
construction methods, or prohibit the
use of riprap or other armoring.
Armoring using riprap or other
materials can be a necessary component
of beneficial aquatic habitat restoration,
establishment, and enhancement
projects.
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We believe that limiting the use of
this NWP for the sole purpose of
restoring streams to historic conditions
would be overly restrictive, and would
effectively prohibit its use for other
beneficial restoration activities. Further,
the pre-construction notification and
reporting requirements for this NWP
will help ensure that activities
conducted under this NWP comply with
the purposes and intent of the NWP, as
well as its terms and condition.
Two commenters said that the
prohibition against stream
channelization conflicts with general
condition 9, Management of Water
Flows, which allows stream restoration
and relocation for some NWP activities.
One commenter suggested that the
Corps remove the channelization
restriction from NWP 27 and expand the
definition of ‘‘stream channelization’’ to
authorize activities beneficial to the
aquatic environment.
As noted above, general condition 9
allows the use of any NWP for projects
that alter the pre-construction course,
condition, capacity, and location of
open waters if they benefit the aquatic
environment. The removal of the stream
channelization prohibition from NWP
27 could inadvertently allow projects to
proceed under this NWP that have more
than minimal adverse impacts on the
aquatic environment. We also believe
that it is unnecessary to modify the
definition of stream channelization as
suggested because the definition
provides an accurate and concise
description of what constitutes stream
channelization.
One commenter recommended
limiting the use of NWP 27 to projects
conducted by or sponsored by state or
federal agencies. One commenter
recommended removing the reference to
prior converted croplands.
We disagree that use of this NWP
should be limited to activities
conducted or sponsored by state or
federal agencies, however, projects not
conducted pursuant to authorities of
other agencies do require a preconstruction notification. The reference
to prior converted croplands in the
reversion provision is necessary, since
prior converted croplands are not
considered to be waters of the United
States (see 33 CFR 328.3(a)(8)).
One commenter suggested including a
definition for shellfish seeding in the
NWP. One commenter questioned
whether the Corps has regulatory
jurisdiction over shellfish aquaculture
and restoration activities. Another
commenter requested clarification
whether pre-construction notification is
required for shellfish seeding authorized
by this NWP. One commenter
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recommended removing the preconstruction notification requirement
for shellfish activities that have the
approval of other government agencies
with resource management
responsibilities. Two commenters said
that state natural resource agencies
should be exempted from the preconstruction notification requirements if
the shellfish seeding activity is done
over an unvegetated bottom, since those
activities are already addressed by other
state and Federal permit processes. Two
other commenters expressed concern
that the proposed changes to the NWP
would adversely affect communitybased shellfish restoration efforts,
including locally-based oyster
restoration programs. They said that the
pre-construction notification
requirements, or requiring any permit
for shellfish restoration, would be
overly burdensome and would
adversely affect community-based
programs that are already operating with
volunteer staffs, minimal budgets, and
limited resources.
We are providing a definition of
‘‘shellfish seeding’’ in the ‘‘Definitions’’
section of the NWPs. This definition
was derived from the definition
provided in the preamble discussion for
proposed NWP D, Commercial Shellfish
Aquaculture Activities (see 71 FR
56275). Shellfish aquaculture and
restoration activities require Department
of the Army authorization, if they
involve discharges of dredged or fill
material into waters of the United States
and/or structures or work in navigable
waters of the United States. On-going
commercial shellfish aquaculture
activities may be authorized by NWP 48
and shellfish restoration activities may
be authorized by NWP 27. New
commercial shellfish aquiculture
activities may be authorized by regional
general permits or individual permits.
The pre-construction notification
requirement is necessary for shellfish
habitat restoration activities, except
those conducted under one of the other
listed authorities, to ensure that those
projects comply with the terms and
conditions of this NWP and do not
cause more than minimal adverse
effects. However, the Corps does not
believe that the PCN requirement is
overly burdensome and it should not
limit the ability of community-based
programs to conduct such activities.
One commenter opposed modifying
this NWP to authorize shellfish
restoration activities because they
believe that these projects can have
more than minimal impact on benthic
habitat. One commenter said that
shellfish seeding should not be
authorized by this NWP. Another
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commenter suggested that fill placement
for shellfish seeding or shellfish bed
preparation activities should not qualify
for any NWP and should only be
evaluated under individual permit
processes. Several commenters
recommended that shellfish seeding
should be authorized by this NWP. A
number of commenters stated that
shellfish seeding can be used to protect
or restore valuable aquatic habitats since
construction of oyster reefs has been
used to attenuate wave energy as part of
coastal restoration strategies.
The restoration of oyster habitat, as
well as the habitat of other shellfish
species, usually provides substantial
benefits to the overall aquatic
environment. Shellfish help improve
water quality and other habitat
characteristics of estuarine and marine
waters. Shellfish seeding is often a
necessary component of restoration
activities, when the objective is to
increase populations of shellfish.
District engineers will review preconstruction notifications or agreements
with other agencies to ensure that these
activities result in minimal individual
and cumulative effects on the aquatic
environment and other public interest
factors. In response to a preconstruction notification, the district
engineer can add special conditions to
the NWP authorization or exercise
discretionary authority and require an
individual permit.
One commenter remarked that
shellfish seeding practices could be
considered an aquaculture activity, and
said that the requirements of NWP 27
could be a significant barrier to
aquaculture development. Another
commenter indicated that projects
solely associated with shellfish
restoration could be authorized by NWP
27, but suggested that it would be more
appropriate to authorize such activities
under the proposed NWP for
commercial shellfish aquaculture
activities. One commenter expressed
concern that NWP 27 may overlap with
NWP 48. One commenter stated that
some oyster restoration and
enhancement is done by commercial
shellfishing operations that harvest only
wild oysters. In some cases, shellfish
husbandry or restoration is required by
other regulatory agencies, and the
commenter stated that neither NWP 27
nor NWP 48 allow this activity. One
commenter asked if each oyster bed
restoration would require a separate
permit, or could an entity apply for a
single permit to cover all of their
shellfish restoration projects. They
recommended establishing a single
permit that any state natural resource
agency could use at any time to
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eliminate the need for those agencies to
obtain separate permits for numerous
individual projects.
This NWP does not authorize
commercial aquaculture activities. It
authorizes shellfish habitat restoration
activities, including shellfish seeding,
that are conducted to restore
populations of shellfish in navigable
waters of the United States. Although
these restored shellfish populations may
be harvested at a later time by licensed
fisherman, the objective of the activities
authorized by this NWP must be to
restore populations of shellfish in
navigable waters of the United States.
This NWP does not authorize structures
or work, such as nets and anchors, that
are used to reduce or eliminate
predation of shellfish growing in these
restored habitats. On-going commercial
aquaculture activities may be authorized
by NWP 48, regional general permits, or
individual permits. New commercial
aquaculture activities may be authorized
by regional general permits or
individual permits. This NWP
authorizes single and complete shellfish
habitat restoration activities. Regional
general permits or individual permits
may be issued by district engineers to
authorize shellfish restoration programs.
This NWP is reissued, with the
modifications discussed above.
NWP 28. Modifications of Existing
Marinas. No changes were proposed for
this NWP. One commenter said that
modifications in special aquatic sites,
such as vegetated shallows or coral
reefs, should require pre-construction
notification. This commenter also
requested clarification whether this
NWP authorizes pile driving, and
recommended requiring preconstruction notification for such
activities.
This NWP authorizes the installation
of piles for the reconfiguration of
marinas. The reconfiguration of existing
marinas generally results in minimal
individual and cumulative adverse
effects, since these activities are limited
to areas currently used for marinas.
Therefore, it is unnecessary to require
pre-construction notification for these
activities. However, division engineers
can regionally condition this NWP to
require pre-construction notification for
activities in certain areas.
This NWP is reissued as proposed.
NWP 29. Residential Developments.
We proposed to modify this NWP by
incorporating the residential
development provisions of NWP 39, so
that there would be one NWP to
authorize single unit and multiple unit
residential developments, including
residential subdivisions. We also
proposed to reduce the scope of
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applicable waters for this NWP, by
prohibiting its use to authorize
discharges of dredged or fill material
into non-tidal wetlands adjacent to tidal
waters. In addition, we proposed to
require pre-construction notification for
all activities.
One commenter requested that a
definition of ‘‘residential property’’ be
provided. This commenter also said that
this NWP should include a provision
prohibiting its use with NWP 39 to
authorize mixed use developments. Two
commenters objected to including
multiple-unit residential developments
in NWP 29 because they felt it is
inconsistent with the original intent of
NWP 29. Several commenters stated that
including multiple-unit residential
development would lead to problems
with water quality certifications or local
government decisions. Two commenters
said that single-family and multi-unit
developments are not similar in nature
while another questioned the need and
the rational for the proposed change.
This NWP utilizes the commonly
accepted definition of what constitutes
a residential property. We do not agree
that there should be a prohibition
against combining NWPs 29 and 39 to
authorize mixed use developments,
because the terms and conditions of
those NWPs, including the preconstruction notification requirements
and general condition 24, Use of
Multiple Nationwide Permits, will help
ensure that those activities will result in
minimal individual and cumulative
adverse effects on the aquatic
environment and other public interest
review factors. As discussed in the
preamble of the September 26, 2006,
Federal Register notice, the proposed
changes effectively eliminate the
previous NWP 29. Previously, single
family residential projects could choose
between NWPs 29 and 39. NWP 39 had
a higher acreage limit, but NWP 29
could allowed activities in wetlands
adjacent to tidal waters. We have
determined that that all residential
projects using an NWP, whether singlefamily or multi-family, should face the
same set of requirements. In particular,
we have determined that residential
projects in wetlands adjacent to tidal
waters should not be authorized through
an NWP, so we are combining all
residential development activities in
NWP 29 and eliminating its use in
wetlands adjacent to tidal waters. We
believe the 1⁄2 acre limit previously
included in NWP 39 will ensure that
projects undertaken only in non-tidal
waters and their adjacent wetlands will
not have more than minimal adverse
effects. Limits for multi-family
residential projects have not changed,
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these activities have merely been shifted
into NWP 29. States concerned with
multiple unit residential developments
may add stipulations to their water
quality certifications that differentiate
between single-family and multi-unit
developments. Local governments can
address their concerns over residential
development through their planning
and zoning processes. Also, the Corps is
expanding the pre-construction
notification requirement to include all
projects authorized under this NWP, to
enhance our ability to identify projects
that may have more than minimal
adverse effects.
One commenter suggested we add
‘‘single-unit residential subdivision’’ to
the list of authorized activates in the
first sentence.
We have added the phrase
‘‘residential subdivision’’ to the list of
activities authorized by this NWP. This
NWP authorizes residential
subdivisions with multiple singlefamily units or multiple-family units.
Several commenters objected to
raising the acreage limit from 1⁄4 acre to
1⁄2 acre. One commenter said that the 1⁄2
acre limit will result in substantial
cumulative losses of waters of the
United States. Two comments
recommended acreage limits of one or
two acres. One commenter asked why
the 1⁄2 acre limit is not for associated
multi-unit developments when it is
expressed as the limit for single-family
residences.
As noted above, the effective acreage
limit for residential projects has not
been raised. We have simply removed
the option of using an NWP with a 1⁄4
acre threshold to authorize single-family
projects in wetlands adjacent to tidal
waters. Through the review of preconstruction notifications, district
engineers will monitor the use of this
NWP so that more than minimal
cumulative adverse effects do not occur.
We disagree that increasing the acreage
limit to one to two acres would result
in activities that have minimal impacts
on the aquatic environment. The 1⁄2 acre
limit applies to any type of residential
subdivision (single-family, multi-family,
or a combination of both), as it did
previously when these projects were
authorized by NWP 39.
Some commenters objected to
requiring pre-construction notification
for all activities, and suggested changing
the pre-construction notification
threshold to 1⁄10 acre. Three commenters
proposed a 1⁄10 acre pre-construction
notification threshold for single-family
developments. Three commenters
supported the proposed preconstruction notification threshold. One
commenter suggested establishing a
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graduated pre-construction notification
threshold based on the size of the
overall development.
We are retaining the requirement for
pre-construction notification for all
activities authorized by this NWP.
Although this will result in an increase
in the number of pre-construction
notifications submitted to district
engineers, we do not believe that it will
be a substantial increase, since many
permittees proposing to construct
residential developments in the past
have submitted verification requests for
NWP 39 authorization even when not
required to do so. The NWP 29 issued
in 2002 require pre-construction
notification for all proposed single
family homes. The pre-construction
notification threshold will also help
ensure compliance with general
condition 17, Endangered Species, and
general condition 18, Historic
Properties. A graduated preconstruction notification requirement
would be unnecessarily complex and
would not provide as much assurance
that only activities with no more than
minimal adverse effects are authorized.
Many commenters discussed the 300
linear foot limit for stream bed impacts.
Those comments are discussed in a
separate section of the preamble. We are
retaining the 300 linear foot limit for
stream bed impacts, as well as the
ability for district engineers to provide
written waivers of the 300 linear foot
limit for losses of intermittent and
ephemeral stream beds.
Several commenters said that this
NWP should retain the requirement to
maintain sufficient buffers adjacent to
all open water bodies, such as streams.
Some commenters stated that a
minimum buffer width should be
required. One commenter supported the
removal of the buffer requirement and
addressing the need for riparian areas
through general condition 20,
Mitigation.
The establishment and maintenance
of riparian areas next to streams and
other open waters will be required by
district engineers as compensatory
mitigation where necessary to ensure
that the authorized work results in
minimal individual and cumulative
adverse effects on the aquatic
environment. Although the NWP 29
issued in 2002 contained a requirement
to establish sufficient vegetated buffers,
the counterpart language in the 2002
NWP 39 reflected the use of vegetated
buffers as components of the
compensatory mitigation plan for the
NWP 39 activity, if there were streams
or other open waters on the project site.
District engineers will make
determinations regarding the
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appropriateness and practicability of
requiring riparian areas, as well as their
width, in the implementation of general
condition 20, Mitigation.
Three commenters said that
residential developments are not water
dependent activities, and therefore,
under the Section 404(b)(1) Guidelines,
an NWP should not be issued unless all
practicable alternatives have been
considered. Some commenters objected
to authorizing attendant features by
NWP 29, because they may not be water
dependent or there may be secondary
impacts associated with the
development.
An activity that is not water
dependent may still be authorized by
NWP as long as an appropriate Section
404(b)(1) Guidelines analysis is
conducted when the NWP is issued. The
decision documents for all NWPs,
including this NWP, that authorize
discharges under Section 404 of the
Clean Water Act include a Section
404(b)(1) Guidelines analysis.
Two commenters objected to
including septic fields as attendant
features and three commenters objected
to including sports fields and golf
courses as attendant features. One
commenter requested a definition of the
term ‘‘integral part’’ to reduce the
potential for authorizing golf courses
that are not directly associated with the
residential development. One
commenter objected to the use of the
NWP for large subdivisions, because of
potential impacts due to sprawl, traffic,
and degradation of water quality.
Septic fields are often necessary
attendant features for residences, and
should be authorized where part of a
single and complete project. Sports
fields and golf courses may also be
integral attendant features of residential
developments. District engineers will
determine, in response to preconstruction notifications, whether golf
courses are integral parts of the
residential development. Impacts of
large subdivisions will be considered
during the pre-construction notification
review process. If such projects would
have more than minimal adverse effects,
these will be addressed through projectspecific special conditions or by
requiring an individual permit.
One commenter requested that we
define ‘‘subdivision’’ as an ‘‘area that
involves all residences that share the
attendant features.’’ One commenter
urged that phased developments be
prohibited since they can result in
impacts to waters that otherwise can be
avoided with comprehensive planning
and permitting.
Defining the term ‘‘subdivision’’ is
unnecessary as there is little confusion
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surrounding the term. Phased
developments can be authorized by the
NWP, provided that each phase is a
single and complete project and has
independent utility. When reviewing
pre-construction notifications, district
engineers will take into account
individual and cumulative impacts of
phased developments. We strongly
support comprehensive planning efforts
undertaken by local governments as a
means of reducing impacts to the
aquatic environment. Where the
cumulative effects of phased projects
would be more than minimal, these will
be addressed through project-specific
special conditions or by requiring an
individual permit.
Four commenters requested that the
NWP authorize projects in non-tidal
wetlands adjacent to tidal waters, while
two comments supported the proposal
to prohibit the use of the NWP in those
areas. One commenter requested a
definition of the term ‘‘adjacent.’’ Two
commenters objected to removal of
language concerning minimization of
on-site and off-site impacts, such as
avoiding flooding of adjacent lands.
Limiting the use of this NWP to nontidal waters of the United States, and
prohibiting its use in non-tidal wetlands
adjacent to tidal waters is necessary to
ensure that this NWP authorizes only
those activities with minimal individual
and cumulative adverse effects on the
aquatic environment. Development
along coastal waters is a growing
concern with significant potential to
cause more than minimal adverse
effects, particularly cumulatively. Such
projects can be authorized by an
individual permit following appropriate
environmental review. The term
‘‘adjacency’’ is defined at 33 CFR
328.3(c). For the NWPs, including NWP
29, requirements to avoid and minimize
impacts to waters of the United States
are addressed through general condition
20, Mitigation.
District engineers will review preconstruction notifications to ensure that
all practicable on-site avoidance and
minimization has been accomplished. In
response to a pre-construction
notification, the district engineer may
require compensatory mitigation to
ensure that the authorized activity
results in minimal adverse
environmental effects (see 33 CFR
330.1(e)(3)).
One commenter said that NWP 29
should not be issued because it results
in more than minimal adverse impacts
particularly when salmonids are
present. One commenter stated that this
NWP should not authorize
impoundments. One commenter said
that there should be an exemption for
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residential developments in coastal
areas in the eastern United States.
Potential impacts to salmon species
are more appropriately addressed
through regional conditions. Division
engineers may regionally condition this
NWP to restrict or prohibit its use in
waters inhabited by salmonids.
Impoundments may be authorized as
attendant features, after reviewing the
pre-construction notification. Section
404 permits are required for discharges
of dredged or fill material into waters of
the United States to construct
residential developments. Such
activities do not qualify for exemptions
under Section 404(f)(1) of the Clean
Water Act.
This NWP is reissued with the
modifications discussed above.
NWP 30. Moist Soil Management for
Wildlife. We proposed to modify this
NWP to allow any landowner to use this
NWP to authorize discharges of dredged
or fill material into non-tidal waters of
the United States for the purpose of
managing wildlife habitat and feeding
areas.
Some commenters supported the
proposed changes to this NWP, since it
will facilitate the production of large
amounts of wetland/wildlife habitat and
conserve the Nation’s native wildlife
populations. However, other
commenters expressed concern about
the use of this NWP by private
landowners, because they may be
creating impoundments to increase
wildlife habitat. One commenter
recommended requiring interagency
coordination to provide guidance to
landowners and to help ensure land
cover types are not detrimentally
converted to other land cover types. One
commenter said that expanding the
NWP to apply to all landowners would
result in more than minimal cumulative
adverse effects.
We believe that it is appropriate to
expand the use of this NWP to private
landowners that have an interest in
attracting and supporting various
species of wildlife on their land. This
NWP does not authorize the
construction of impoundments, because
it does not authorize new roads, dikes,
and water control structures. We believe
that it is not necessary to require
interagency coordination for these
activities because only activities that do
not result in a net loss of aquatic
resource functions and services are
authorized. The terms and conditions
and the ability of division engineers to
impose regional and case-specific
conditions on this NWP, will ensure
that the activities authorized by this
NWP will result in no more than
minimal individual and cumulative
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adverse effects on the aquatic
environment.
One commenter recommended
imposing a 1⁄2 acre limit on activities
conducted by private landowners. One
commenter recommended adding preconstruction notification requirements
to this NWP, so that district engineers
can review proposed activities to ensure
that they comply with the terms and
conditions of the NWP. One commenter
indicated that this NWP should
authorize moist soil management
activities for native vegetation that are
not necessarily for wildlife use.
Since this NWP authorizes only ongoing wildlife management activities
involving moist soil management, we do
not believe it is necessary to impose an
acreage limit or require pre-construction
notification for these activities. Division
engineers can regionally condition this
NWP to require pre-construction
notification, if there are concerns for the
aquatic environment or other public
interest review factors that may need to
be addressed through case-specific
review of these activities. Moist soil
management activities conducted
primarily for growing native plants may
be authorized by other NWPs, regional
general permits, or individual permits.
Restoration of wetland meadows,
forested wetlands, and other native
plant communities may also be
authorized by NWP 27.
One commenter suggested changing
the title of this NWP to ‘‘Maintenance of
Existing Moist Soil Management Areas
for Wildlife.’’ One commenter
recommended modifying the ‘‘Note’’ at
the end of this NWP to acknowledge
that maintenance may be exempt under
Section 404(f) of the Clean Water Act.
We do not agree that it is necessary
to change the title of this NWP, because
the text of the NWP clearly states that
is authorizes only soil management for
on-going, site-specific, wildlife
management activities. We have
modified the ‘‘Note’’ to include a
statement concerning the section 404(f)
exemption.
This NWP is reissued with the
modification discussed above.
NWP 31. Maintenance of Existing
Flood Control Facilities. We proposed to
remove the last sentence of the first
paragraph of this NWP. In addition, we
proposed to add levees to the list of
features that can be maintained through
the authorization provided by this NWP.
A few commenters stated support for
the addition of levees to the list of
features that can be maintained with
authorization under this NWP. In
addition, one commenter recommended
that the Corps exempt or develop a
streamlined NWP for federally
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constructed or funded levees where
maintenance responsibilities for those
levees have reverted to a local agency.
We believe that the NWP program is
already a streamlined permit process
and discharges associated with federally
constructed and funded flood control
projects which have reverted to a local
agency should still be subject to the
requirements of this NWP, including the
establishment of a maintenance
baseline. At this time, we believe it is
necessary to conduct a site specific
verification through the preconstruction notification process to
ensure that the adverse effects of the
project are no more than minimal. The
Corps has no authority to exempt
discharges of dredged or fill material
that occur in conjunction with the
maintenance of the facility, or to waive
any requirement for necessary
mitigation. The inclusion of levees in
this NWP does not preclude
maintenance of levees that is allowed
under other NWP authorizations, such
as NWP 3.
One commenter stated that, as flood
control projects constructed by the
Corps and transferred to a non-federal
sponsor have a Corps-developed
Operations and Maintenance (O&M)
manual, and the sponsor is obligated to
perform maintenance according to the
O&M manual, the project’s as-built
drawings and O&M manual should
constitute the maintenance baseline.
Therefore, no maintenance baseline
submittal should be required.
The intent of this NWP is to require
the submittal of a maintenance baseline
for all projects requesting authorization
by this NWP. A non-federal sponsor can
submit the as-built drawings and O&M
manual from a federally-constructed or
funded flood control project. In any case
the maintenance baseline must be
approved by the district engineer.
Another commenter suggested that
the requirement to submit best
management practices (BMPs) with the
maintenance baseline documentation be
eliminated, as BMPs are addressed by
several general conditions. This
commenter also requested that we
clarify the important exception that
applies to this NWP in regard to the
general condition 27 requirement that
the district engineer must approve any
compensatory mitigation proposal
before the permittee commences work.
The Corps disagrees that the
requirement to submit BMPs is
adequately addressed by general
conditions. We believe that inclusion of
the BMPs in the documentation is
necessary so that the Corps can ensure
that the impacts associated with the
activity will be no more than minimal.
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In addition, the inclusion of certain
BMPs may reduce the impacts to the
aquatic environment and, as a result, the
required one-time mitigation associated
with establishing the baseline. The
BMPs submitted with the maintenance
baseline documentation do not preclude
the Corps from requiring additional
BMPs that might be necessary to ensure
that the maintenance activity results in
minimal adverse effects on the aquatic
environment. Regarding mitigation
approval, we believe the proposed text
of this NWP clearly states that for this
NWP, the district engineer will not
delay necessary maintenance so long as
the district engineer and permittee
establish a schedule for identification,
approval, development, construction
and completion of any such required
mitigation. It also states that work can
begin before approval of the
maintenance baseline in emergency
situations.
Two commenters opposed adding
levees to the list of features that can be
maintained through authorization by
this NWP. One of these commenters
believed that the change constitutes
more than a wording change, because
levees are large scale structures with
impacts that require a thorough
assessment. The other commenter stated
that levees disrupt natural processes
important to floodplains and habitat.
They also noted that the presence of
levees on a stream does not transform
the stream into a flood control facility.
While we agree that the construction
of levees may require a thorough
assessment of impacts on the watershed,
the maintenance of existing levees is an
activity that is appropriate for inclusion
in this NWP since levees are often
integral parts of flood control facilities.
This NWP does not authorize the
construction of levees. We believe that
the limitations and general conditions
associated with the NWP will ensure
that authorized projects will have no
more than minimal adverse effects. The
requirement for an approved baseline
and the ability to require mitigation
provides a safeguard for valuable
habitat. The Corps agrees that levees do
not make a stream a flood control
facility. However, levees are a flood
control facility and this NWP should
allow maintenance of the levees. In
order for flood control activities to occur
in the stream, they would have to be
included in the maintenance baseline,
as described in the text of the NWP.
One commenter observed that the text
of this NWP uses the phrase
‘‘significantly reduced capacity’’ when
discussing abandonment. They stated
that Regulatory Guidance Letter 87–2
discusses the ramification of using the
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word ‘‘significant’’ in Corps
documentation and suggested that it be
changed. Another commenter said that
this NWP should not authorize actions
that need to be taken because of neglect.
We believe that the use of the word
‘‘significantly’’ in this NWP is not
contrary to the Regulatory Guidance
Letter because it describes a level of
reduction in flood capacity and does not
relate to any determination of
environmental impacts. If a flood
control facility can be considered
abandoned because of neglect, then the
NWP would not authorize the work
needed to reconstruct that facility.
Another commenter requested that
the fill associated with beaver dam
control and maintenance be added to
the list of features authorized by this
NWP. While the Corps agrees that the
maintenance of beaver dam control and
maintenance structures may be
authorized by this NWP, this NWP does
not authorize fills associated with the
construction of new structures.
Two commenters opposed removing
the last sentence in the first paragraph
of this NWP (regarding types of
maintenance activities that do not
require section 404 permits) because
they believe that the language clarified
that vegetation maintenance does not
require a section 404 permit. The Corps
believes that this sentence is
unnecessary, since Section 404 permits
are only required for discharges of
dredged or fill material, and, per the
regulations at 33 CFR 323.2(d)(3)(ii),
vegetation removal above the ground,
that does not disturb the root system or
include redeposition of excavated soil
material, is not a discharge of dredged
or fill material.
One commenter stated that many
existing flood control facilities may not
have met the criterion (i.e., it was
previously permitted by the Corps, it
did not require a permit at the time it
was constructed, or it was constructed
by the Corps and transferred to a nonfederal sponsor), or the permittee cannot
provide documentation that the
criterion was met. Another commenter
requested that this NWP authorize the
maintenance of projects that were built
by others but accepted as part of a
federal flood control project or those
that are authorized under state or local
flood control laws. Both commenters
requested that the Corps modify or
eliminate the criterion listed in the first
sentence of this paragraph and authorize
maintenance of any flood control
facility after approving the maintenance
baseline and reviewing the activity
through the pre-construction
notification process. In addition, one
commenter stated that the Corps should
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not consider a flood control facility to
be abandoned because vegetation has
become established in the facility. That
commenter also said that the NWP
should compel agencies to perform
maintenance more frequently by
requiring mitigation for temporal losses
in vegetation or habitat. Another
commenter stated that agencies should
be encouraged to reduce the frequency
of maintenance where feasible by
approving maintenance baselines that
allow for less frequent maintenance.
One commenter said that this NWP
should also authorize temporary
stockpiling as authorized by NWP 12.
The criteria in the first sentence of
this NWP cover all properly authorized
flood control facilities. Unless a flood
control facility was constructed as a
result of a Corps Civil Works project, it
would have required a Corps permit
unless it was constructed in a manner
that did not require Corps authorization
or it was exempt from permit
requirements. If it should have had
Corps authorization but did not, we do
not think it is appropriate to authorize
maintenance under this NWP. The
Corps will not generally require
documentation of compliance with
these criteria, unless there is reason to
believe that these criteria are not met.
We believe that the current text
accurately describes how a site should
be determined to be abandoned. The
presence of vegetation does not
necessarily indicate that a flood control
facility has been abandoned. However, a
site may be determined to be abandoned
when vegetation has substantially
diminished the capacity of the channel.
We do not believe it is necessary to
require permittees to conduct
maintenance more frequently, to
prevent the establishment of vegetation
within the flood control facility. The
one-time mitigation requirement is
sufficient to offset the losses of aquatic
resource functions and services that will
occur as a result of keeping the facility
within the maintenance baseline.
Maintenance-related discharges that do
not exceed the established maintenance
baseline will not result in losses of
aquatic resources beyond those
addressed at the time the maintenance
baseline is established. The frequency of
maintenance will depend on the
characteristics of the flood control
facility and the surrounding area. Those
flood control facilities that were
constructed in more dynamic
environments generally require more
frequent maintenance. Because of the
various environmental factors affecting
the need for maintenance and the
physical parameters that apply to an
existing facility, it would be difficult to
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establish a maintenance baseline that
lessens the frequency of maintenance.
We do not believe it would be
appropriate to modify this NWP to
authorize temporary stockpiling of
sediments and other materials in waters
of the United States. Sediments and
other materials removed during the
maintenance of flood control facilities
must be deposited at non-jurisdictional
areas, unless the district engineer
authorizes temporary stockpiling
through a separate Department of the
Army authorization.
The previous commenter also
remarked that the provisions for
emergency situations still require that
the permittee submit a pre-construction
notification and wait for Corps approval
before conducting any emergency work
within the flood control facility. They
stated that this requirement could
compromise public health and safety, as
it typically takes one or two days,
minimum, to obtain the necessary
approval to proceed. They requested
deferral of the pre-construction
notification requirement until after the
emergency maintenance activities have
been conducted. We believe that NWP
31, as proposed, is a reasonable and
prudent way to minimize the burdens
imposed on permittees, within the
constraints of applicable law and
regulation. It is not appropriate to defer
the submittal of a pre-construction
notification, due to the fact that the
Corps must determine if authorization
by this NWP is applicable. The Corps
has developed specific procedures for
dealing with emergency situations.
Entities responsible for maintaining
flood control facilities should contact
their local Corps office well in advance
of the rainy season, to familiarize
themselves with the available
emergency processing procedures for
that district.
One commenter suggested that
activities authorized by this NWP
instead be authorized by NWP 3. We
believe that the specific requirements of
this NWP are necessary to ensure that
impacts to the aquatic environment are
minimal. Incorporating these
requirements into NWP 3 would be
confusing and make implementation of
that NWP more difficult.
Another commenter asserted that this
NWP has the potential for more than
minimal impacts, based on the fact that
there are no limits on acreage or volume
of discharges. The commenter also
commented that one-time mitigation
does not adequately ensure that aquatic
functions will be restored, and that
limiting mitigation to one-time will
result in more than minimal adverse
impacts if mature wildlife habitat is
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destroyed repeatedly. The Corps
believes that activities authorized by
NWP 31 that comply with the
maintenance baseline provision do not
result in more than minimal impacts,
even without acreage limitations. The
establishment of the maintenance
baseline, in effect, identifies the location
and physical dimensions of waters of
the United States that have been
incorporated in the flood control
facility. Discharges that result in losses
of these waters (i.e., that exceed the
maintenance baseline) are not eligible
for authorization under NWP 31. In light
of this, we believe that the ‘‘one-time
mitigation requirement’’ imposed in
conjunction with the establishment of
the maintenance baseline is sufficient
for the purpose of this NWP. The intent
of the one-time mitigation is to replace
the aquatic functions that may be lost
each time maintenance is performed.
Once the mitigation is in place, any
aquatic functions that develop between
maintenance activities, are over and
above the level of function that existed
before the initial maintenance occurred.
For areas or projects with specific
issues, the division and district engineer
may choose to add regional conditions
or special conditions to the NWP
authorization.
One commenter made reference to a
particular project containing salmonids
and stated that an NWP should not have
been issued for that particular project.
The commenter objected to this NWP
authorizing the continued maintenance
of the project because the salmonid
habitat may have partially recovered
and would be repeatedly impacted.
While we agree that this can occur, we
do not agree that requiring mitigation
over and over for what is, in effect, the
same impact is appropriate. We believe
that the limitations and general
conditions included within this NWP
will ensure that it will result in no more
than minimal effects. The requirement
for an approved baseline and the ability
to require mitigation provides a way to
safeguard valuable habitat.
This NWP is reissued as proposed.
NWP 32. Completed Enforcement
Actions. We proposed to eliminate the
phrase ‘‘For either (i), (ii), or (iii)
above,’’ from the last paragraph of this
NWP. In addition, we proposed to
remove the phrase ‘‘or fails to complete
the work by the specified completion
date.’’
Two commenters suggested that the
five-acre non-tidal water or one-acre
tidal water limits be eliminated. They
believe that if the NWP applied to
enforcement actions with greater
impacts, then the mitigation could be
completed earlier which would reduce
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temporal losses. One commenter said
that the NWP should have a limit of two
acres for wetland impacts, since the
permit process, including the
opportunity for public comment, has
been avoided. One commenter stated
that individual permits should be
required for activities undertaken as a
result of an enforcement action. They
believe that greater oversight is
appropriate for a party that broke the
law.
We believe that if the unauthorized
activity impacts more than five acres of
non-tidal waters or one acre of tidal
waters that it may be more appropriate
to either require an individual permit
review or to pursue a judicial settlement
or judgment. In cases where judicial
settlements are pursued, there is usually
a comprehensive evaluation of the
environmental damage associated with
the unauthorized work and substantial
mitigation and penalties. In addition,
we recognize that the limits for this
NWP exceed the limits for the majority
of the NWPs. We believe however, that
the requirement that non-judicial
settlements provide for environmental
benefits equal to or greater than the
environmental harm caused by the
unauthorized activity ensures that the
net impacts caused by the unauthorized
work are no more than minimal. The
thresholds limit the maximum size of
the impact area and, wherever
appropriate and practicable, restoration
of this area will be required to undo the
impacts. In any case, full compensation
for the impacts in some form is
required.
One commenter requested we delete
the sentence stating that the NWP does
not apply to any activities occurring
after the date of the court decision,
decree or agreement that are not for the
purpose of mitigation, restoration or
environmental benefit. The commenter
believes that this provision limits the
ability of the Corps to enter into a
settlement agreement. Another
commenter requested that language be
added to the NWP to expressly prohibit
its use for any future impacts related to
the existing project that is under the
enforcement action.
The Corps believes that the NWP as
proposed is appropriate. Proposed
additional project impacts (e.g., impacts
necessary to complete the project that
was initiated without a permit) must be
evaluated under other NWPs, regional
general permits, or individual permit
review processes. This permit is
intended only to authorize past
discharges along with the required
compensatory activities, not to
substitute for applicable permit
requirements for future activities.
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One commenter remarked that the
activities authorized by this NWP do not
correlate with the programmatic general
permits in the commenter’s state.
The Corps acknowledges this
comment, however, we believe it is
simply a statement and does not warrant
any changes to the proposed NWP.
This NWP is reissued as proposed.
NWP 33. Temporary Construction,
Access, and Dewatering. We proposed
to divide the first sentence of this NWP
into two sentences, to clarify that the
NWP can be used to authorize
temporary activities associated with
both construction projects that do not
otherwise require permits from the
Corps or the U.S. Coast Guard, and
those that do require and have obtained
such permits. We also proposed to move
the requirement for a restoration plan
from the ‘‘pre-construction notification’’
general condition (general condition 13
of the 2002 NWPs) to the ‘‘Notification’’
paragraph of this NWP, because it only
applies to this NWP. We inadvertently
used the term ‘‘mitigation plan’’ in the
‘‘Notification’’ paragraph in the
proposed NWP, and have changed it to
‘‘restoration plan’’ in the final permit.
The pre-construction notification must
include a restoration plan showing how
all temporary fills and structures will be
removed and the area will be restored to
pre-project conditions. The restoration
plan should also describe reasonable
measures for avoidance and
minimization of adverse effects to
aquatic resources. Please note that this
restoration plan is different from the
mitigation requirements in general
condition 20 for permanent losses of
waters of the United States. We
proposed to remove the sentence that
states that the district engineer will add
special conditions to ensure minimal
adverse effects, since the addition of
special conditions where necessary to
ensure minimal adverse effects is a
condition of all NWPs.
One commenter suggested that NWP
33 should also be used to authorize
temporary stockpiles and temporary fills
that are related to construction
activities.
The Corps agrees that this work could
potentially be authorized under NWP 33
as long as all other conditions are met
and the work is the minimum necessary
to complete the project. However, the
districts have discretion in determining
if the work is the minimum necessary.
One commenter expressed concern
about the last statement in this NWP,
which requires a Section 10 permit for
structures left in place. The commenter
indicated this statement is contradictory
since any structures left in place would
be permanent and would not qualify for
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the NWP 33 anyway. The commenter
recommends removing or clarifying this
statement.
This statement is intended to reiterate
that if any structures are left in place,
separate authorization is required,
however we have broadened it to cover
all situations where structures left in
place require separate Section 10
authorization.
Another commenter generally
supported NWP 33 as proposed, but
recommended changing the word
‘‘conditions’’ to ‘‘contours’’ in the
sentence stating ‘‘Following completion
of construction, temporary fill must be
entirely removed to upland areas,
dredged material must be returned to its
original location, and the affected areas
must be restored to the pre-project
conditions.’’ Several commenters
indicated that requiring the area to be
restored to pre-project conditions may
not be beneficial when the pre-project
conditions were degraded. One
commenter suggested we require the
affected areas be restored to the preproject conditions or to a condition with
greater than pre-project habitat
functions and services. Another
commenter suggested saying that the
area should be returned to appropriate
pre-existing stable elevations and slope
and restored with vegetation species
matching the adjacent undisturbed
areas, but consistent with the purposes
of the associated project for which the
temporary construction is necessary.
We agree that returning a degraded
area to better than pre-existing
conditions is beneficial and we support
this concept. We will not require the
area to be restored to create better
habitat functions and services, but we
are not precluding this work from
occurring. Removal of temporary fills is
also addressed in general condition 13
and the language in NWP 33 has been
slightly modified to match this general
condition. Any fill left in place will
require separate authorization.
One commenter questioned whether
the restoration plan for temporary and
permanent impacts could be included in
a single plan, with any proposed
mitigation, and whether the mitigation
plan must be submitted concurrently
with the pre-construction notification.
Another commenter opposed the
provision requiring that a restoration
plan be included in the pre-construction
notification that shows how the area
will be restored to pre-project
conditions. The commenter was
concerned that a restoration plan is not
always developed up front because a
contractor is often not selected until
after a permit has been issued.
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The pre-construction notification
must contain a restoration plan showing
how all temporary fills and structures
will be removed and the areas restored
to pre-project conditions. The
restoration plan must, at a minimum,
include a general description of how
restoration will be accomplished, with
as much detail as is practicable when
the pre-construction notification is
submitted. We do not believe that
selection of a contractor is necessary for
the development of an appropriate
restoration plan.
Several commenters requested that we
clarify or define some of the terms in
NWP 33, such as cofferdam, access fill,
and temporary structure. One of the
commenters also asked if the Corps
considers temporary construction pads
to be a form of access that requires
authorization. They also asked if
cofferdam includes structures that only
partially isolate a portion of the
streambed but still allow water to pass.
The Corps believes that cofferdam,
access fill, and temporary structure are
widely used and accepted terms. The
Corps is hesitant to place strict
definitions on these terms. The Corps
does consider temporary construction
pads to be a form of access that can be
authorized under NWP 33 and we do
consider a structure that partially blocks
a portion of the streambed to be a
cofferdam that could be authorized by
NWP 33.
One commenter suggested that
notification should not be required for
temporary impacts that last less than 24
hours, when used with Best
Management Practices. Another
commenter requested we include a limit
on the duration of impacts, such as 48
hours. Another commenter requested
that the Corps consider an exemption to
the pre-construction notification
requirement if the temporary fill is a
mat instead of dirt, or a stabilized
material, and it is in place for only a
short time, such as 48 hours. This
commenter also suggested that the
Corps allow an exemption to the preconstruction notification requirement
for minor amounts of temporary
impacts. A commenter questioned
whether a water-inflated cofferdam
would be considered de minimus and be
exempt from submitting a preconstruction notification. Several
commenters recommended that a PCN
should not be required for temporary
construction access roads and other
construction activities covered under
NWP 33, unless the discharge causes the
temporary loss of greater than 1⁄10 acre
of waters of the United States.
We have modified NWPs 3, 12, and 14
to address concerns regarding pre-
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construction notification and temporary
impacts to waters of the United States.
In particular, we are not requiring
separate authorization under NWP 33
for temporary impacts associated with
activities authorized under these three
NWPs. Therefore, we are retaining the
pre-construction notification
requirements from the September 26,
2006, proposal for NWP 33. We have
modified the text of this NWP to require
restoration of affected areas to preconstruction elevations, with
revegetation, as appropriate, to be
consistent with the changes to general
condition 13, Removal of Temporary
Fills.
This NWP is reissued with the
modification discussed above.
NWP 34. Cranberry Production
Activities. We proposed to rearrange the
text of the NWP and to eliminate the
phrase ‘‘provided the activity meets all
of the following criteria’’. In addition,
we proposed to eliminate the
requirement for delineations of special
aquatic sites from the text of the NWP,
since this is a requirement of general
condition 27.
One commenter requested
clarification of the last part of the last
sentence which reads ‘‘. . .and the NWP
would authorize that existing operation,
provided the 10-acre limit is not
exceeded.’’ Another commenter
recommended reducing the acreage
limit to 1⁄2 acre. This commenter also
said that pre-construction notifications
must clearly indicate areas to be
impacted by the proposed activity.
We believe that the text of this NWP
is clear. This NWP only authorizes
activities associated with existing
cranberry production operations, such
as expansion, reconfiguration or
leveling. The NWP provides
authorization for these types of
activities, provided the total impacts to
waters of the United States during the
5-year term of the NWP do not exceed
10 acres. It does not authorize the
construction of new cranberry
production operations. Since this NWP
authorizes only existing cranberry
production activities, the 10-acre limit
is appropriate because these areas
remain as wetlands, even though they
are managed to improve cranberry
production. General condition 27
requires prospective permittees to
submit delineations of waters of the
United States with their preconstruction notifications, so that the
impacts of the proposed activity can be
assessed.
Some commenters asserted that the
activities authorized by this NWP will
result in more than minimal adverse
impacts, individually and cumulatively.
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These commenters also requested that
the Corps not reissue this permit as it
violates section 404(e) of the CWA and
the section 404(b)(1) Guidelines. In
addition, they remarked that it is
unclear how the permittee would
determine whether a net loss occurs.
They were concerned that permittees
would claim that converting a natural
wetland to a cranberry bog does not
result in a net loss of wetlands and as
a result these losses would not be
counted. In addition, one commenter
remarked that the Corps should not rely
on compensatory mitigation to offset the
potential adverse impacts associated
with conversion of wetlands to
cranberry bogs.
We believe that the activities
authorized by this NWP will not have
more than minimal impacts both
individually and cumulatively. This
NWP authorizes activities associated
with the expansion, enhancement, or
modification of existing cranberry
operations. This NWP does not
authorize new operations. Regarding the
determination of net loss, this NWP
requires pre-construction notification.
The district engineer will determine if
the proposed project would result in a
net loss of wetland acreage, not the
permittee. In making this determination,
the Corps would consider conversion of
natural wetlands to cranberry bogs a
loss of waters. We believe the preconstruction notification requirement
gives district engineers the ability to
assess the impacts to aquatic resources
and, if the acreage limit is exceeded or
if otherwise warranted, exercise
discretionary authority and require an
individual permit. The individual
permit process includes case-specific
reviews to ensure compliance with the
Section 404(b)(1) Guidelines. In
addition, division and district engineers
will condition such activities where
necessary to ensure that these activities
will have no more than minimal adverse
effects on the aquatic environment,
individually and cumulatively. The
Corps believes that this NWP is fully in
compliance with section 404(e) of the
Clean Water Act.
One commenter stated that the Corps’
limited cumulative effects data suggests
a reduction in average impacts
associated with this NWP. They added
that this reduction appears to be due to
cranberry production activities being
authorized under state or regional
general permits.
We believe that the use of state
programmatic and regional general
permits to authorize cranberry
operations are appropriate. All general
permits must have no more than
minimal adverse effect. Regional general
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permits developed in consideration of
local and regional issues have been
determined to have minimal impacts
both individually and cumulatively. As
with the NWPs, regional general permits
also enable the district engineer to
exercise discretionary authority to
require individual permit review, where
appropriate.
The NWP is reissued as proposed.
NWP 35. Maintenance Dredging of
Existing Basins. We proposed to change
the phrase ‘‘disposed of’’ to ‘‘deposited
at’’ in the text of this NWP.
One commenter suggested the NWP
be modified to allow disposal of
dredged material (e.g., sand and gravel)
in the littoral system.
We believe the placement of dredged
material at upland sites with the
implementation of proper siltation
controls helps to ensure minimal
impacts on the aquatic environment,
individually and cumulatively. We
agree that beneficial use of dredged
material, including placement of
suitable material on beaches or in the
littoral zone, can provide environmental
benefits. However, such activities can
result in unintended adverse
environmental effects, and therefore
require detailed and comprehensive
analysis of sediment and littoral
processes. We believe that an individual
permit is the appropriate mechanism for
authorizing this use of dredged material
and that it should not be permitted
under this NWP.
Another commenter requested that we
require pre-construction notification to
help determine whether dredging
activities authorized under this NWP
may indirectly adversely impact
adjacent beaches and near shore habitat.
Generally, dredging of existing basins
does not result in substantial adverse
impacts to adjacent beaches and/or near
shore habitat when proper siltation
controls are used, as required by this
NWP. We disagree that pre-construction
notification is necessary for these
dredging activities since division
engineers have the ability to impose
regional conditions, including the
requirement for pre-construction
notifications for certain activities, to
ensure minimal adverse effects on the
aquatic environment, individually and
cumulatively.
One commenter remarked that we
should provide clarification on the
applicability of this NWP to existing
access channels and mooring facilities.
This NWP authorizes excavation and
removal of accumulated sediment for
maintenance of existing basins provided
that the activity complies with its terms
and conditions.
This NWP is reissued as proposed.
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NWP 36. Boat Ramps. We proposed to
modify this NWP to allow district
engineers to waiver the 50 cubic yard
limit for discharges of dredged or fill
material into waters of the United States
to construct a boat ramp. We also
proposed to allow district engineers to
waiver the 20 foot width limit for boat
ramps. These waivers can be issued
only if, after reviewing a preconstruction notification, the district
engineer determines that adverse effects
on the aquatic environment and other
factors of the public interest will be
minimal.
Many commenters supported the
discretion vested in district engineers to
waive the limitations imposed by this
NWP, however one commenter objected
to the flexibility provided to the district
engineers and suggested activities that
exceed 50 cubic yards or 20 feet in
width be evaluated under an individual
permit process. Another commenter
requested we include guidelines for
when and to what degree the district
engineer would apply waivers to the 50
cubic yard fill limit and/or 20-foot
width limit to avoid inconsistencies.
We believe deference must be given to
district engineers’ expertise and
knowledge of the local aquatic
environment, as well as his/her
assessment of information submitted in
pre-construction notifications, to make
case-specific determinations on the
effects to the aquatic environment. The
proposed pre-construction notification
requirement for discharges that exceed
50 cubic yards or 20 feet in width will
enable the district engineer to evaluate
the direct, indirect and cumulative
effects of a proposed activity to
determine whether a waiver is
appropriate or an individual permit is
required. Because of the inherent
variability across the nation, we
disagree that it is necessary or
appropriate to establish guidelines for
the application of the waiver. We expect
district engineers to formulate their
case-specific determinations on the
appropriateness of the waiver based on
the unique characteristics of the local
aquatic environment and in
consideration of the specific
circumstances of the proposed activity.
One commenter noted that boat ramps
are hardened surfaces that diminish
near shore or bank habitat and asserted
that pre-construction notification
should be required along with
mitigation.
We believe that the discretion vested
in district engineers to issue special
conditions on a case-specific basis,
including requirements for appropriate
and practicable mitigation (see general
condition 20), will ensure that losses to
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the aquatic environment are adequately
offset. We also believe that the ability of
division engineers to impose regional
conditions for certain activities will
ensure minimal adverse effects on the
aquatic environment, individually and
cumulatively.
Two commenters indicated that the
case-by-case waiver of the 50 cubic yard
and 20-foot width discharge limits
should also require the Corps to
coordinate with appropriate federal and
state natural resource agencies.
We disagree it is necessary to
coordinate with federal and state natural
resource agencies prior to the district
engineer determining whether to grant a
waiver for those activities that exceed
the 50 cubic yard fill limit and/or 20foot width limit. District engineers have
the aquatic resources expertise to
determine whether activities will result
in more than minimal adverse effect on
the aquatic environment.
One commenter noted that activities
authorized under this NWP do not
require Department of the Army
authorization in Section 404-only
waters unless there is more than
incidental fallback.
Discharges in waters of the United
States that are not otherwise exempt
from regulation require Corps
authorization. We acknowledge that the
Corps does not regulate excavation
under section 404 in instances when
there is only incidental fallback.
This NWP is reissued as proposed.
NWP 37. Emergency Watershed
Protection and Rehabilitation. We
proposed to rearrange the text of this
NWP to match the other permits. In the
final permit, we have added two
additional types of activity (reclamation
of abandoned mine lands pursuant to
Title IV of SMCRA and the Emergency
Conservation Program administered by
the Farm Service Agency) that may be
authorized.
One commenter supported the
reissuance of this NWP without change,
since they regularly partner with the
Natural Resources Conservation Service
on emergency projects. Another
commenter expressed concerns that
NWP 37 does not contain specific
requirements for conducting repair work
and it only includes generic references
to environmentally defensible
approaches. The commenter agreed that
allowing the work to commence
immediately (with follow-up permitting
as necessary) may be desirable due to
the urgency of some disaster responses;
however, they indicated that the process
may be prone to uncertainty about
requirements and may cause more than
minimal harm to the aquatic resources.
The commenter indicated that activities
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are funded by the Natural Resources
Conservation Service but not always
implemented by the agency, so people
with limited experience may be
completing the work. The commenter
suggested that work should only be
allowed to proceed prior to verification
where a damage response team
comprised of federal and state agencies
have developed the site specific plans
for damage repair.
We believe that in some cases the
urgency of the activities authorized by
this NWP requires an expedited process.
All activities require pre-construction
notification, and as a general matter, the
prospective permittee should wait until
the district engineer issues an NWP
verification before proceeding with the
watershed protection and rehabilitation
activity. A watershed protection and
rehabilitation activity may proceed
immediately only in those cases of true
emergencies (i.e., where there is an
unacceptable hazard to life or a
significant loss of property or economic
hardship will occur). Where practicable,
permittees are encouraged to consult
informally with the Corps before
proceeding with emergency activities. In
cases where emergency watershed
protection and rehabilitation activities
were conducted prior to receiving an
NWP verification, the district engineer,
after reviewing the pre-construction
notification, may modify, suspend, or
revoke the NWP authorization through
the procedures at 33 CFR 330.5. All of
the projects authorized by this permit
are conducted under the sponsorship of
another Federal resource management
agency. Those agencies, not the Corps,
have the responsibility to determine
whether the project complies with their
program authority. The Corps must
determine the applicability of the NWP
to the specific project, but for the most
part, the Corps only reviews the
proposed work to determine compliance
with the requirements of the NWP and
the general conditions. We believe that
any specific concerns should be
addressed through regional conditions
or through consultation with the
sponsoring agency.
A couple of commenters
recommended adding Title IV of the
Surface Mining Control and
Reclamation Act, which governs the
abandoned mine land reclamation
program, to proposed NWP E, Coal
Remining Activities. One commenter
suggested adding to NWP 37 work
funded by the Farm Service Agency
under its Emergency Conservation
Program, which rehabilitates farmland
damaged by natural disasters.
As discussed below, we have revised
proposed NWP E (now designated as
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NWP 49), to authorize abandoned
mined land reclamation activities that
also involve coal extraction activities.
However, for those abandoned mine
land reclamation activities that do not
involve coal extraction, we believe it is
more appropriate to authorize these
activities under NWP 37, since they
help protect and rehabilitate
watersheds, and have revised the text of
the NWP accordingly. In cases where it
is necessary to conduct an emergency
abandoned mine reclamation activity
immediately, the project proponent may
proceed with the work (see paragraph
(d)(3) of general condition 27) while the
district engineer reviews the preconstruction notification. For clarity, we
have also added a new paragraph to this
NWP that is consistent with paragraph
(d)(3) of general condition 27. We have
also added Emergency Conservation
Program activities funded by the Farm
Service Agency, which provides costshare assistance to eligible participants
to rehabilitate farmland damaged by
floods, hurricanes, or other natural
disasters. The implementing regulations
for the Emergency Conservation
Program are found at 7 CFR part 701.
The NWP is reissued, with the
modifications discussed above.
NWP 38. Cleanup of Hazardous and
Toxic Waste. We proposed to modify
this NWP by moving the requirement to
submit a delineation of waters of the
United States to paragraph (b)(4) of the
‘‘pre-construction notification’’ general
condition (GC 27). We also proposed to
move the last sentence of this NWP to
a ‘‘Note’’ at the end of the NWP.
One commenter requested this NWP
be revoked, because the cleanup of
hazardous waste has the potential to
cause adverse effects during and after
the activities. The commenter indicated
that remedial activities in navigable
waters and wetlands need site-specific
review, evaluation and permitting to
ensure proper design, appropriate
restoration, and long term stability.
This NWP requires pre-construction
notification to the Corps. We believe our
review under this NWP is sufficient,
since the activities authorized must be
performed, ordered, or sponsored by a
government agency with established
legal or regulatory authority.
Another commenter suggested the
expansion of this NWP to allow removal
of waste material, such as trash, debris,
detritus, or rubble, in waters of the
United States. The commenter suggested
that the NWP should be modified to
authorize the immediate removal of the
waste and the notification to the Corps
after the material has been removed.
In general, the removal of waste
material should not require Corps
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authorization, unless the activity
involves discharges of dredged or fill
material into waters of the United States
and/or structures or work in navigable
waters of the United States. Temporary
access to remove the material may be
authorized by NWP 33. Restoration of
the affected area may be authorized
under NWP 27.
One commenter requested
clarification regarding the applicability
of NWP 38 for emergency response to an
oil release in waters of the United States
from electrical equipment that is not
covered by a Spill Prevention, Control,
and Countermeasure (SPCC). The
releases are governed by EPA’s
polychlorinated biphenyl spill response
regulations (40 CFR part 761). Because
the activities are not included in a SPCC
Plan, they are not authorized by NWP
20. The work that is required must be
initiated within 24 or 48 hours of
discovery of the release, so the
commenter requested that either NWP
20 be modified or the pre-construction
notification requirement under NWP 38
be removed in situations where the
response time is critical.
Instead of modifying this NWP, we
have modified NWP 20 to include
coverage of response to spills not
covered by a SPCC Plan, but otherwise
required to be initiated in a short time
frame by another government agency,
such as EPA’s polychlorinated biphenyl
spill response regulations at 40 CFR part
761.
This NWP is reissued as proposed.
NWP 39. Commercial and
Institutional Developments. We
proposed to modify this NWP by
moving the provisions authorizing
residential developments to NWP 29,
requiring pre-construction notification
for all activities authorized by this
NWP, and applying the 300 linear foot
limit to ephemeral streams.
Three commenters objected to moving
residential developments from NWP 39
to NWP 29 because these developments
are inconsistent with the original intent
of NWP 29. Six commenters supported
removing residential developments
stating that the impacts associated with
residential developments are not the
same as commercial and institutional
developments. Three commenters
desired the ability to use multiple NWPs
with NWP 39 for mixed-use
developments, such as housing and
commercial. One commenter did not
support removing residential
development from this NWP because
mixed-use developments would lead to
more than minimal impacts if multiple
NWPs were used.
As discussed in the preamble to the
September 26, 2006, Federal Register
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notice, the proposed changes effectively
eliminates the previous NWP 29. We do
not believe that NWP 39 will result in
more than minimal individual and
cumulative adverse effects, on the
aquatic environment if it is used with
other NWPs in accordance with general
condition 24, Use of Multiple
Nationwide Permits.
Two commenters recommended
allowing the NWP to be used in nontidal wetlands adjacent to tidal waters,
while another agreed with the proposed
language to exclude its use from these
wetlands. One commenter declared that
the NWP should not be used in
wetlands accessible to anadromous fish
or in difficult-to-replace aquatic
environments. One commenter wanted
the acreage limit increased to 5 acres
and another recommended it be
decreased to 1⁄4 acre so that it reflects
the limits in the previous version of
NWP 29.
We believe that restricting the types of
wetlands the NWP applies to is an
appropriate method of assuring that
minimal adverse impacts are not
exceeded. Division engineers may
regionally condition or revoke this NWP
in certain areas or for certain activities
if they believe the NWP would result in
more than minimal impacts. Increasing
the acreage limit to 5 acres would likely
result in activities that will have more
than minimal individual and
cumulative adverse effects on the
aquatic environment. Reducing the
acreage limit to 1⁄4 acre would cause
many projects that do have minimal
adverse impacts to be evaluated under
the individual permit process.
Many commenters supported
retaining the language requiring
sufficient vegetated buffers to be
maintained adjacent to all open water
bodies, such as streams. One commenter
requested an unspecified minimum
vegetated buffer width while two
commenters suggested a 200 foot
setback from streams containing
anadromous fish. One commenter
supported removing of the buffer
language and relying on paragraph (d)
(now designated as paragraph (f)) of
general condition 20.
In general, the Corps agrees that
buffers (i.e., riparian areas) are
necessary to protect streams and other
open waters. District engineers will
make determinations regarding the need
for and amount of required riparian
areas in the context of general condition
20, Mitigation.
One commenter stated that including
the expansion of commercial or
institutional buildings will lead to
piecemealing projects and result in
more than minimal impacts on the
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aquatic environment. Five objected to
removing language concerning
avoidance and minimization to the
maximum extent practicable. Two
commenters suggested maintaining
language requiring a conceptual
mitigation plan. Several commenters
recommended retaining the language
concerning single and complete
projects. Two commenters asserted that
maintaining language addressing
minimal change to flow and water
quality was necessary. Two commenters
objected to removal of language
concerning minimizing on-site and offsite impacts, such as avoiding flooding
of adjacent lands. Another commenter
objected to removing ‘‘many’’ of the
restrictions in the NWPs, including this
one. One commenter suggested that
problems will occur without the
language about ‘‘single and complete
projects.’’
We disagree with these comments.
Requirements for avoidance and
minimization, management of water
flows, and water quality are provided in
the NWP general conditions. Removal of
language from the permit text itself does
not affect the applicability of
requirements contained in Corps
regulations and in the NWP general
conditions. We have repeatedly
emphasized in this preamble that
permittees must review the general
conditions before using any NWP to
ensure that they are meeting all
requirements for its use. District
engineers will review pre-construction
notifications to ensure that all
practicable on-site avoidance and
minimization has been accomplished. In
response to a pre-construction
notification, the district engineer may
require compensatory mitigation to
ensure that the authorized activity
results in minimal adverse
environmental effects (see 33 CFR
330.1(e)(3)).
Several commenters objected to the
mandatory pre-construction notification
requirement and suggested a preconstruction notification threshold of
1⁄10 acre or greater than 300 feet of
stream loss. Some of these commenters
reasoned that eliminating the 1⁄10 acre
pre-construction notification threshold
would be a disincentive to avoid the
loss of waters of the United States. Two
commenters supported the proposed
pre-construction notification
requirement.
We disagree that the pre-construction
notification threshold should be 1⁄10
acre. We acknowledge that this will
result in an increase in the number of
pre-construction notifications district
engineers receive, however, we are
proposing to simplify the information
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required in a pre-construction
notification (see general condition 27) to
reduce the paperwork burden on
prospective permittees. Requiring
notification for all activities authorized
under NWP 39 will help ensure adverse
minimal effects.
Thirteen commenters wrote
concerning impacts to streams and the
use of waivers. See the discussion
regarding this topic, above.
One commenter stated that projects
authorized by this NWP are not waterdependent and should not be permitted.
We agree that most commercial and
institutional developments are not water
dependent activities. This does not
mean that they cannot be permitted,
only that they undergo an alternatives
analysis (see the EPA’s 404(b)(1)
Guidelines at 40 CFR part 230).
Although analysis of off-site alternatives
is not required for general permits, each
proposed project is evaluated to
determine whether avoidance and
minimization has been accomplished on
the project site to the maximum extent
practicable (see general condition 20,
Mitigation). In addition, the activity is
not authorized under an NWP if the
adverse impacts to waters of the United
States are more than minimal.
This NWP is reissued as proposed.
NWP 40. Agricultural Activities. We
proposed to modify this NWP to require
pre-construction notification for all
activities, authorize the construction of
farm ponds in waters other than
perennial streams, and remove certain
restrictions on who could use the NWP.
One commenter wanted to retain the
paragraph numbering of the 2002 NWP.
Another commenter said that this NWP
should be limited to USDA program
participants.
The Corps believes the revised
numbering system is appropriate and
easy to understand. This NWP should
not be limited to USDA program
participants, since there are agricultural
activities being conducted by nonparticipants that result in minimal
adverse effects on the aquatic
environment which are appropriately
authorized by NWP.
One commenter opposed reissuance
of NWP 40 because of unacceptable
impacts to wetlands. Two commenters
did not support eliminating the 1⁄2 acre
limit per farm tract on impacts to waters
of the United States, and one
commenter recommended reducing the
acreage limit to 1⁄10 acre. One
commenter expressed concern that
removing farm tracts as the basis for the
acreage limit would result in use of this
NWP to authorize discharges of dredged
or fill material for non-agricultural
activities. One commenter stated that
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roadside stands should not be
considered farm buildings for
authorization under this NWP. One
commenter recommended retaining the
1⁄10 acre threshold for pre-construction
notification. One commenter stated that
pre-construction notification should not
be required for projects conducted
under USDA programs.
We believe the requirement for preconstruction notifications for all
activities and the case-by-case review by
district engineers will ensure that
activities authorized by this NWP result
in no more than minimal individual and
cumulative adverse effects to the aquatic
environment and other public interest
review factors. The district engineer will
add case specific conditions and require
mitigation when needed to ensure
impacts do not exceed the minimal
level, and will assert discretionary
authority to require an individual
permit when impacts are more than
minimal. Due to differences in program
requirements between USDA programs
and Section 404 of the Clean Water Act,
it is not possible to ensure that activities
conducted under USDA programs will
necessarily comply with Section 404
requirements and have minimal adverse
impact to waters of the United States.
Therefore, we are retaining the preconstruction notification requirement
for USDA program participants and
projects. We have removed the reference
to ‘‘farm tracts’’ because we have found
that it caused confusion in the past. The
limit applies to each single and
complete project (see definitions
section). District engineers will
determine during the pre-construction
notification process whether the acreage
limit is satisfied. Eliminating the use of
farm tracts would not expand the use of
this NWP to non-agricultural activities.
The text of this NWP clearly states that
it authorizes only agricultural activities.
One commenter objected to
authorizing farm ponds in wetlands and
two objected to authorizing farm ponds
in non-tidal waters excluding perennial
streams. One commenter supported the
use of NWP 40 for construction of farm
ponds only in streams without aquatic
life use designations. Another
commenter said that the proposed
modification was unnecessary, since
many farm ponds are constructed
outside of waters of the United States or
they are exempt from section 404 permit
requirements because of the exemption
at Section 404(f)(1)(C) of the Clean
Water Act. This commenter expressed
concern that the proposed changes to
NWP 40 would require landowners to
submit pre-construction notifications for
all farm ponds, even if they are not
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States or they qualify for the section
404(f) exemption.
We are limiting the construction of
farm ponds to certain types of waters
where the adverse effects to the aquatic
environment are likely to be minimal,
individually and cumulatively. This
NWP does not authorize the
construction of farm ponds in perennial
streams. Under this NWP, farm ponds
may be constructed in non-tidal
wetlands, intermittent streams, and
ephemeral streams. Pre-construction
notification is required for all activities
authorized by this NWP, so that district
engineers will have the opportunity to
review each proposed activity to
determine whether the adverse effects
on the aquatic environment will be
minimal. If the construction of a farm
pond does not involve discharges of
dredged or fill material into waters of
the United States, or if it qualifies for a
Section 404(f) exemption, the project
proponent is not required to submit a
pre-construction notification. This NWP
authorizes the construction of farm
ponds that involve discharges of
dredged or fill material into waters of
the United States and do not qualify for
the Section 404(f)(1)(C) exemption,
because of the recapture provision at
Section 404(f)(2). We have added a
sentence to the ‘‘Note’’ at the end of this
NWP to clarify that this NWP is used to
authorize the construction of farm
ponds that are not exempt under
Section 404(f).
One commenter was concerned about
negative impacts to salmonids from
agriculture activities. Of main concern
was placement of farm buildings in
wetlands and streams, discharges from
drainage tiles into farm ditches that
were built in salmonid streams, and
levee maintenance that degrades
salmonid habitat and riparian areas.
Potential adverse impacts from these
activities will be addressed during the
pre-construction notification review.
Water quality issues are also addressed
during Section 401 water quality
certification or by a Clean Water Act
Section 402 permit.
Two commenters stated that the
proposed permit will destroy wetland
acres. One commenter stated that the
loss of prairie potholes and western
glaciated potholes will be staggering.
Another commenter stated that
discharges into playas, prairie potholes,
and vernal pools should not be allowed
under NWP 40.
The 1⁄2-acre limit for this NWP applies
to the loss of waters associated with
activities authorized by this NWP.
During the pre-construction notification
review process, if the district engineer
determines that adverse effects to
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aquatic resources are more than
minimal, individually or cumulatively,
he or she will impose special conditions
to reduce the impacts to the minimal
level or assert discretionary authority
and require an individual permit. In
addition, division engineers may add
regional conditions to this NWP to
restrict or prohibit its use in certain
types of waters, if discharges into those
waters for agricultural activities would
result in more than minimal adverse
effects on the aquatic environment.
General condition 20, Mitigation,
requires district engineers to determine
appropriate and practicable mitigation
necessary to ensure that impacts are no
more than minimal. The Corps believes
the pre-construction notification
requirement for all activities and the
case-by-case review by district engineers
will ensure that activities authorized
under this NWP will result in no more
than minimal individual and
cumulative adverse effects to the aquatic
environment. The Corps notes that the
acreage and linear foot limits in the
NWPs apply only to waters that are
jurisdictional under the Clean Water
Act.
One commenter stated that the Corps
now proposes to ignore impacts to
waters of the United States associated
with agricultural dredge and fill
activities that are deemed exempt under
Section 404(f) of the Clean Water Act.
This NWP authorizes certain
agriculture activities that are not eligible
for the exemptions under Section 404(f)
of the Clean Water Act. Those
agricultural activities that qualify for the
Section 404(f) exemptions do not
require a Section 404 permit. This has
always been the case; it is not a change
from current practice.
One commenter stated that the
possible waiver for the relocation of
greater than 300 linear feet of existing
serviceable drainage ditches constructed
in intermittent and ephemeral streams
would result in more than minimal
adverse impacts. Another commenter
said that the provision authorizing the
relocation of existing serviceable
drainage ditches constructed in nontidal streams should be conditioned to
ensure that the activity does not result
in a reduction in base flow to the
stream.
In response to a pre-construction
notification for the proposed relocation
of greater than 300 linear feet of existing
serviceable drainage ditches constructed
in intermittent or ephemeral streams,
the activity is not authorized unless the
district engineer issues a written waiver
after determining that the activity will
result in minimal adverse effects on the
aquatic environment. The relocation of
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drainage ditches must also comply with
general condition 9, Management of
Water Flows, to maintain the capacity of
those waters to the maximum extent
practicable.
Several commenters stated that some
language in the NWP was confusing or
needed clarifying. This included the
phrase ‘‘ditches constructed in waters of
the United States’’, whether the permit
applies to farm tracts or the entire farm,
and the concept of ‘‘necessary for
agriculture production’’.
We have removed the definition of
’’farm tract’’ and the conditions limiting
the use of NWP 40 on a particular site,
since district engineers will receive preconstruction notifications for all
activities authorized by this NWP.
District engineers will review preconstruction notifications for those
NWPs to ensure that the proposed work
results in minimal individual and
cumulative adverse environmental
effects. We believe that the other terms
are self-explanatory. Determining
whether an activity is necessary for
agriculture production involves some
discretion, which the district engineer
will apply when evaluating preconstruction notifications for proposed
projects.
One commenter said that this NWP
should not authorize the construction of
livestock watering ponds unless the
applicant submits documentation
showing that he or she has obtained
government assistance for the
construction of the pond, and that no
feasible alternatives are available that
would avoid discharges into waters of
the United States. This commenter
supported the proposed prohibition
against constructing farm ponds in
perennial streams, but also
recommended that the NWP prohibit
the construction of farm ponds in
oxbows or lakes. Another commenter
stated that NWP 40 should authorize the
construction of aquaculture ponds.
We do not agree that it is necessary
to require prospective permittees to
obtain government assistance as a
condition of authorization under this
NWP. General condition 20, Mitigation,
requires permittees to avoid and
minimize adverse effects to waters of
the United States to the maximum
extent practicable on the project site.
District engineers will also review preconstruction notifications to ensure
compliance with the terms and
conditions of this NWP, including
general condition 20. If a farm pond is
proposed to be constructed in an oxbow
or a lake, the district engineer will
review the pre-construction notification
to determine if the activity will result in
minimal adverse effects. In addition,
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division engineers may also regionally
condition this NWP to restrict or
prohibit its use to construct farm ponds
in certain categories of non-tidal waters
of the United States. We believe that
construction of aquaculture ponds is a
distinct activity that should not be
authorized under this NWP because
there may be unique issues associated
with it (e.g., invasive species concerns,
changes in water quality). Ponds
constructed for purposes other than
conventional agriculture may be
authorized under other general permits
or individual permits.
This NWP is reissued as proposed.
NWP 41. Reshaping Existing Drainage
Ditches. We proposed to modify this
NWP to clarify that it authorizes only
the reshaping of drainage ditches
constructed in waters of the United
States where the purpose of reshaping
the ditch is to improve water quality. As
a result of this modification, we also
proposed to remove the sentence that
states why compensatory mitigation is
not required for the activities authorized
by this NWP.
The purpose of this NWP is to
encourage landowners who need to
maintain drainage ditches constructed
in waters of the United States to do so
in a manner that benefits the aquatic
environment. The maintenance of a
drainage ditch is exempt under Section
404(f)(1)(C) of the Clean Water Act, and
does not require a section 404 permit.
This exemption does not apply to the
reshaping of existing drainage ditches,
so landowners have a disincentive to
reshape their ditches, even though such
reshaping can be beneficial to the
aquatic environment. This NWP
authorizes those reshaping activities
that benefit the aquatic environment.
This NWP was first issued on March
9, 2000, (65 FR 12818) to authorize, to
the extent that a section 404 permit is
required, the grading of the banks of a
currently serviceable ditch to gentler
(shallower) slopes than its current or
original configuration. Reshaping a
drainage ditch so that it has shallower
side slopes can help improve water
quality by decreasing the velocity of
water flowing through the ditch and by
spreading out water flow over a greater
area of soil surface. It should also
provide more area for plants to become
established and grow within the ditch.
These changes are likely to help
improve water quality by increasing
water contact with vegetation and soil
microbes, which facilitates the removal
of nutrients and other chemical
compounds through biogeochemical
processes. Slower water flow rates
through the ditch should also decrease
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erosion, further improving water
quality.
We proposed to remove the
prohibition against permanent
sidecasting of excavated material into
waters of the United States, where the
excavated material results from the
ditch reshaping activity. In cases where
there are jurisdictional wetlands or
other waters next to the ditch to be
reshaped, this prohibition is likely to
cause many landowners to maintain the
ditch at its originally designed
configuration to qualify for the
exemption, since the 404(f)(1)(C)
exemption allows discharges of dredged
or fill material into waters of the United
States resulting from ditch maintenance
activities.
Some commenters supported the
modifications to this NWP because they
encourage landowners to maintain
drainage ditches in a manner that
benefits the aquatic environment.
Several commenters also agreed with
the proposal to remove the prohibition
against permanent sidecasting of
excavated materials into waters of the
United States. Several other commenters
did not support allowing permanent
sidecasting of material excavated from
reshaped ditches. These commenters
suggested that the sidecasting would
have adverse impacts that exceed the
water quality improvements. One
commenter suggested we provide
conditions on the sidecast material,
such as requiring the fill to be no higher
than 18 inches, so that the hydric soils
will retain their hydric characteristics.
They also suggested requiring random
distribution of the material and that the
sidecast should not interfere with
surface water flows. Another commenter
indicated that permanent sidecasting
that isolates wetlands on-site, rendering
them non-jurisdictional, should not be
allowed.
The exemption at 404(f)(1)(C) allows
sidecasting, but prohibits reshaping
drainage ditches. This NWP provides an
incentive to improve water quality
through reshaping the drainage ditches
while still allowing sidecasting of the
material. The Corps believes that
allowing the sidecasting under this
NWP will encourage landowners to
reshape existing drainage ditches in
favor of water quality improvements
instead of conducting traditional
maintenance activities. The Corps
recognizes the need to ensure that the
sidecasting has minor impacts on the
aquatic environment and does not
isolate wetlands. Regional conditions
may be added to ensure that the
individual and cumulative impacts are
minimal. We note that the presence of
a man-made berm between wetlands
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and adjacent waters does not necessarily
make the wetlands non-jurisdictional.
Some commenters suggested that
many drainage ditches are within what
was a historical stream that has been
straightened and many of these drainage
ditches are used by anadromous
salmonids as transport to upstream
spawning grounds and for juvenile
rearing. One commenter suggested this
NWP should not be used in waterbodies
bearing salmon where a state or federal
watershed analysis or limiting factors
analysis has determined that off-channel
rearing habitat is limiting or potentially
limiting to salmonid production. The
commenters indicated that an
individual permit should be required for
work in ditches that are accessible to
anadromous salmonids. The commenter
suggested if this NWP is utilized in such
waterbodies, a regional condition
should require a delineation of pools
and riffles and that reshaping be
conducted in a manner that does not
reduce volume and surface area of pools
or other suitable low velocity habitat.
The Corps agrees that these are
important concerns but they only relate
to certain areas. Division and district
engineers will impose regional
conditions or case-specific conditions,
so that adverse effects to salmon species
that utilize these drainage ditches are
minimal, individually and
cumulatively.
One commenter suggested this NWP
should allow for the restoration of
ditches that lose their original shape,
become vegetated, and obtain
characteristics of wetlands due to long
ditch maintenance cycles, which are
often greater than 20 years.
The Corps believes that this NWP may
potentially be used in such areas in
cases where the purpose of the work is
to improve water quality. However, to
be eligible to use this NWP, the drainage
ditches must be currently serviceable
and not so degraded that the area
appears to have more the characteristics
of a wetland than those of a drainage
ditch.
One commenter suggested this NWP
should authorize reshaping of natural
drainage features. The commenter
indicated that reshaping unvegetated
streambeds, channels, and watercourses
with vertical banks subject to
continuous erosion would provide
flatter and vegetated side slopes, which
would improve water quality.
We do not agree that this NWP should
be modified to authorize alterations to
the geomorphology of natural streams
and other waters of the United States.
Such changes to natural waterbodies
may result in more than minimal
adverse effects to the aquatic
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environment. Other forms of
Department of the Army authorization
may be more appropriate to authorize
this type of work.
Another commenter indicated that the
amount of change in reshaping is not
specified.
We do not believe it is necessary to
place a limit on the cubic yards of
change that can occur with this permit.
We believe if the purpose is to reshape
the ditch and improve water quality, an
upper limit does not need to be
specified.
One commenter indicated that the
term ‘‘* * * ditches constructed in
waters of the United States’’ is
confusing and suggested changing it to
‘‘serviceable drainage ditches which
were constructed in regulated wetlands
or by channelizing waters of the United
States.’’ Another commenter stated that
the Corps has too narrowly defined
what constitutes a drainage ditch. The
commenter indicated that a large
number of streams in the United States
have had some channelization and some
people refer to these water bodies as
drainage ditches. The commenter is
concerned that some natural
waterbodies will be reshaped, which
would actually reduce water quality.
We believe the current phrasing is
simple and concise, since jurisdictional
wetlands are waters of the United
States. This NWP is intended for
currently serviceable drainage ditches
and the applicability of the NWP can be
determined on a case-by-case basis by
the district engineers. This NWP does
not authorize the channelization of
existing streams and it does not
authorize the relocation of those
streams. In addition, this NWP does not
authorize the reshaping of natural
waterbodies. If a ditch has become
incised, this NWP may potentially be
used to reshape the ditch, thereby
making it more stable.
Another commenter is concerned
about the lack of required
documentation or demonstration of how
the proposed reshaping will meet this
basic condition of NWP eligibility. The
commenter also questioned why the
Corps does not define the term
‘‘improving water quality’’ and does not
explain how to evaluate a project that
improves some aspects of water quality,
but harms others. One commenter
suggested a wording change to say, ‘‘for
the purpose of stabilizing eroded banks’’
instead of ‘‘for the purpose of water
quality.’’ The commenter indicated that
saying the work is for the purpose of
improving water quality is vague and
subject to misinterpretation.
The work authorized by this permit is
designed to improve water quality by
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regrading the drainage ditch with
gentler slopes, which can reduce
erosion, increase growth of vegetation,
and increase uptake of nutrients and
other substances by vegetation. We have
added this language to the NWP. More
stable banks may result from these
activities, but the primary objective of
these projects is to improve water
quality. We recognize that the
environmental benefits of these
activities usually need to be determined
subjectively.
A commenter was also concerned that
the NWP does not require an applicant
to prove the proposed ditch reshaping
activity will not increase the area
drained by the ditch. The commenter is
concerned this NWP has a high
potential for abuse and will attract
landowners looking for authorization to
make their ditches larger to drain
wetlands more thoroughly and they
suggest that the Corps will need to
dedicate more resources to track and
monitor the use of this permit. The
commenter also indicated there must be
a limit on the extent of impacts
authorized under this permit and that
extensive reshaping of drainage ditches
should be subject to individual permit
review.
The Corps believes that the preconstruction notification requirement
for this NWP will allow us to review
larger-scale proposals and ensure that
additional wetlands are not drained by
the work. We have modified the text of
this NWP, to prevent drainage of
additional wetlands. We have replaced
the phrase ‘‘original design capacity’’
with ‘‘original as-built capacity’’ to
reflect the extent of drainage that
occurred when the drainage ditches
were originally constructed. We have
also changed the word ‘‘designed’’ to
‘‘constructed’’ in that sentence to ensure
that the reshaping activity does not
drain additional waters. We believe
these changes will help prevent
increases in the area drained by these
ditches, especially in those cases where
the ditch did not achieve its design
capacity when it was originally
constructed.
A commenter recommended
modifying the requirement that the
capacity of the ditch must be the same
as originally designed. The commenter
is concerned that the only way for the
capacity to remain the same is if the
side slopes are increased is to narrow
the bottom of the existing ditch. The
commenter expressed concern about
narrowing the bottom of the ditch and
still having a stable system. The
commenter suggested requiring the
bottom width and depth of the ditch to
be the same as originally designed.
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We do not agree that this language
should be changed, except to refer to the
as-built capacity or the original
construction of the ditch, for the reasons
discussed above. The Corps believes
that changing the language as
recommended in the previous paragraph
may unduly restrict the design criteria,
because there may be some cases where
the bottom width and depth would
change, but the capacity would remain
the same; therefore, we are keeping the
current language. The important point is
that this NWP may not be used to
increase the capacity of the ditch.
A commenter requested that some
provisions be made to allow for an
increase in capacity to accommodate
increased drainage in the watershed.
Due to increased runoff, ditches may
have become incised and restoring
stable slopes may require increased
capacity. The commenter suggested not
restricting the permit to original design
capacity, since this does not allow for
laying back the side slopes without
decreasing maximum depth to avoid
increasing cross sectional area. Another
commenter indicated that there may be
constricted conditions that do not allow
for shallow side slopes and wanted to
know if there would be flexibility in the
use of NWP 41.
Modifying this NWP to allow
increased drainage capacity would be
contrary to the intent of the NWP,
which is to authorize changes in the
ditch that help improve water quality. If
the site characteristics do not support
reshaping the ditch in a manner that
improves water quality, without
increasing drainage capacity, then this
NWP cannot be used. Modifications of
drainage ditches to accommodate
changes in watershed hydrology or site
limitations may be authorized by other
types of Department of the Army
permits.
One commenter asked if the NWP 41
would authorize the reshaping of
existing drainage ditches that were not
constructed in waters of the United
States but now contain an ordinary high
water mark or wetlands.
This NWP may be used in currently
serviceable drainage ditches to the
extent that they are jurisdictional.
Division or district engineers can make
a determination on the applicability of
this NWP on a case-by-case basis.
A commenter was concerned about
the prohibition against stream
channelization activities. The
commenter suggested that activities that
modify the cross sectional configuration
of drainage ditches could easily be
interpreted as manipulation of a
stream’s condition that causes more
than minimal interruption of normal
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stream processes. The commenter
encouraged the Corps to remove the
channelization restriction from NWP 41.
The intent of this NWP is to authorize
the reshaping of ditches to provide more
stable conditions, which will improve
water quality. The Corps does not
believe this permit should allow
channelization of streams.
Several commenters questioned why
this NWP excludes non-tidal wetlands
adjacent to tidal waters. The
commenters asked why it matters
whether currently serviceable drainage
ditches were originally constructed in
non-tidal wetland adjacent to tidal
waters or in upland settings.
We believe that excluding ditch
reshaping activities in non-tidal
wetlands adjacent to tidal waters is
necessary to ensure that the adverse
effects on the aquatic environment will
be minimal, individually and
cumulatively. Wetlands adjacent to tidal
waters tend to have a high level of
ecological and hydrologic connectivity
with tidal waters. Ditch reshaping
activities in these areas may have more
than minimal adverse effects and can be
better addressed by other general
permits or individual permits.
One commenter stated that this NWP
should have a 500 linear foot limit and
a 250-foot pre-construction notification
threshold and that mitigation must be
required for all adverse impacts to the
aquatic environment authorized under
this permit. Another commenter said
that the activities authorized by this
NWP would result in more than
minimal adverse effects.
The Corps believes that the preconstruction notification threshold is
sufficient. Since we will see all
proposals that are over 500 linear feet,
we will have the opportunity to
determine if the impacts are more than
minimal. The Corps does not believe
this NWP will cause a permanent loss
of waters, since the work involves
reshaping existing drainage ditches to
improve water quality, therefore,
mitigation is not required.
Several commenters suggested that
removing some of the language from the
NWP 41 issued in 2002 made the permit
less clear. One commenter suggested
that the Corps add language stating
indicating that this NWP is limited to
reshaping activities that would restore
more natural stream characteristics such
as increasing the area of riparian
vegetation through regrading or
recreating stream meanders.
The Corps believes that including this
type of language would go beyond the
intent of this NWP, which is to
authorize the reshaping of existing
drainage ditches that may not have ever
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contained meanders or other natural
stream characteristics.
Other commenters suggested putting
the language from the 2002 NWP 41
about compensatory mitigation back in
the NWP.
The Corps agrees and the following
language has been placed in the final
version of NWP 41: ‘‘Compensatory
mitigation is not required because the
work is designed to improve water
quality.’’
This NWP is reissued with the
modifications discussed above.
NWP 42. Recreational Facilities. We
proposed to modify this NWP by
removing the language that limits its use
to those recreational facilities that are
integrated into the existing landscape
and do not substantially change preconstruction grades or deviate from
natural landscape contours. We also
proposed to modify this NWP to require
pre-construction notifications for all
activities, and apply the 300 linear foot
limit for losses of stream bed to
ephemeral streams. In addition, we
proposed to modify this NWP, to
authorize the construction of ski areas,
playing fields, and basketball and tennis
courts.
One commenter suggested that the
Corps change the word ‘‘loss’’ to ‘‘fill’’
or ‘‘impact’’ (including temporary and
permanent impacts). Another
commenter suggested rewording a
sentence to address the Rapanos and
Carabell decisions.
The Corps believes that the term
‘‘loss’’ is the appropriate term. The term
‘‘loss of waters of the United States’’ is
defined in the ‘‘Definitions’’ section of
the NWPs. Issues related to the
jurisdictional reach of the CWA are not
addressed in the NWPs or this
preamble. Department of the Army
Section 404 permits are required only
for activities involving discharges of
dredged or fill material into
jurisdictional waters.
Three commenters stated that the
activities authorized by this NWP are
not similar in nature, and will not result
in minimal adverse effects to water
quality and the aquatic environment.
This NWP authorizes recreational
facilities. The activities authorized by
this NWP are all recreational facilities,
which is a category of activity that is
similar in nature. The pre-construction
notification requirement gives district
engineers the ability to assess the
impacts to aquatic resources and, if
warranted, exercise discretionary
authority to add special conditions or
require individual permits. Division and
district engineers will condition such
activities where necessary to ensure that
these activities will have no more than
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minimal adverse effects on the aquatic
environment, individually and
cumulatively.
Two commenters supported the
removal of the limits on the types of
recreational activities that can be
authorized by this NWP. A number of
commenters objected to allowing
changes in preconstruction grades and
deviations in natural landscape
contours. Two commenters requested
we prohibit the use of this NWP for golf
courses, ski areas, playing fields, and
basketball and tennis courts because
these types of facilities are likely to alter
natural landscape contours. One
commenter stated that projects such as
golf courses that require filling large
valleys to create flatter areas, will
change the hydrology of the area. One
commenter requested that the Corps
revoke this NWP or exclude golf
courses, ski slopes, campgrounds and
associated structures from this NWP. A
couple of commenters suggested
prohibiting the use of this NWP for
habitat conversion, and the construction
of buildings, stables and parking lots.
Another commenter supported
excluding hotels, racetracks, stadiums,
and arenas from authorization by this
NWP. A few commenters stated the
proposed NWP encourages development
of recreational facilities in wetlands,
which creates maintenance problems,
and they requested the NWP not be
modified.
The Corps believes that recreational
facilities that result in minimal
individual and cumulative adverse
effects on the aquatic environment
should be authorized by this NWP,
regardless of the changes that might
occur to pre-construction grades or
natural landscape contours in areas not
subject to section 404 jurisdiction. This
is consistent with activities authorized
by other NWPs, which do not restrict
grading and landscape contouring in
uplands. Because of the preconstruction notification requirement
for this permit, the district engineer will
have the opportunity to review
proposed recreational facilities to
determine if they will result in more
than minimal individual and
cumulative adverse effects.
Six commenters objected to the
proposal to allow district engineers to
waive the 300 linear foot limit in
ephemeral and intermittent streams.
The district engineer will only waive
the 300-linear foot limit in ephemeral
and intermittent streams if he or she
determines that the individual and
cumulative adverse effects on the
aquatic environment are minimal. Any
waivers must be issued in writing from
the district engineer.
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Two commenters requested that the
NWP be clarified so that acreage limits
are applied cumulatively for both the
original construction and expansion.
One commenter said that this NWP
should not be used with NWPs 29 or 39,
to authorize recreational facilities
within residential, commercial, or
institutional developments, and that the
1⁄2 acre should apply to such projects.
The NWPs authorize single and
complete projects, as defined in the
‘‘Definitions’’ section of the NWPs. The
1⁄2-acre limit associated with this NWP
applies to a single and complete project.
In any case, if the district engineer
determines that the impacts of a
proposed project are more than
minimal, individually or cumulatively,
he or she will assert discretionary
authority and require an individual
permit. It is not necessary to prohibit
the use of NWP 42 with NWPs 29 or 39.
Even though NWPs 29 and 39 may be
used to authorize recreational facilities
as attendant features of residential,
commercial, or institutional
developments, any use of NWP 42 with
NWPs 29 or 39 would be limited by
general condition 24, Use of Multiple
Nationwide Permits. Under that general
condition, the 1⁄2 acre limit would apply
to such projects.
Two commenters supported requiring
pre-construction notification for all
activities authorized by this NWP. In
addition, they stated that the Corps
should require documentation in the
pre-construction notification that the
facilities will result in unaltered surface
and groundwater regimes and will not
alter flow into open waters or streams.
Another commenter supported retaining
the 1⁄10 acre threshold for preconstruction notifications and
eliminating it completely for projects
conducted under USDA programs. The
commenter believed requiring preconstruction notifications for all
activities makes more work for both the
public and the Corps.
The Corps believes that preconstruction notifications are necessary
to ensure that proposed activities will
result in no more than minimal
individual and cumulative adverse
impacts. If the district engineer
determines that the construction or
expansion of recreational facilities will
result in adverse effects on aquatic
resources, including water regimes and
flow, he or she can impose special
conditions or require an individual
permit.
One commenter opposed the
prohibition on use of this NWP in nontidal wetlands adjacent to tidal
wetlands, stating that it is arbitrary.
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We believe that prohibiting the use of
this NWP to authorize discharges of
dredged or fill material into non-tidal
wetlands adjacent to tidal waters to
construct or expand recreational
facilities is necessary to ensure that the
NWP authorizes only those activities
that result in minimal individual and
cumulative adverse effects on the
aquatic environment. Non-tidal
wetlands adjacent to tidal waters
warrant greater protection because of
their interactions with those tidal waters
and the functions and services they
provide to coastal ecosystems.
Construction activities resulting in
discharges of dredged or fill material
into those waters are more appropriately
addressed through the individual permit
process or regional general permits.
One commenter stated that recreation
facilities proposing impacts in streams
accessible to anadromous salmonids
should not be authorized by this NWP.
Another commenter request that the
Corps place regional conditions on this
NWP such that it will not authorize the
construction of trails or paths along the
top bank of a stream unless there is no
loss of riparian vegetation or the
riparian vegetation can grow back. That
commenter also suggested that this
NWP should not be used with NWP 13,
since activities authorized by these two
NWPs may adversely affect the addition
of woody material in stream channels.
Division engineers can impose
regional conditions on this NWP to
address cumulative impacts, including
impacts to salmon habitat. We do not
agree that NWP 13 should be prohibited
from being used with this NWP for a
single and complete project. Bank
stabilization may be required to
maintain the integrity and safety of a
recreational facility and to protect
aquatic resources.
One commenter stated that the preconstruction notification requirement is
not enough to ensure minimal impacts
and that the Corps position that adverse
impacts will be offset by compensatory
mitigation is unfounded. This
commenter also opposed eliminating
the requirement to submit avoidance
and minimization statements and water
quality management measures.
The pre-construction notification
requirement allows the Corps to
evaluate recreational facilities on a caseby-case basis and determine if the
project, as proposed, will result in more
than minimal impact. The Corps
believes that compensatory mitigation is
an appropriate means of ensuring that
adverse effects on the aquatic
environment are minimal. The
requirement to demonstrate avoidance
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and minimization is part of general
condition 20, Mitigation.
One commenter said that this NWP
should be conditioned to require the
establishment and maintenance of
buffers adjacent to all open waters,
streams, and wetlands on the site, to
prevent water quality degradation due
to erosion and sedimentation, protect
stream banks, provide wildlife habitat,
and to enhance watershed functions and
values.
The establishment and maintenance
of riparian areas next to streams and
other open waters is addressed through
the requirements of general condition
20, Mitigation. Please see the preamble
discussion for general condition 20,
where we address comments concerning
requirements and recommended widths
for riparian areas.
This NWP is reissued as proposed.
NWP 43. Stormwater Management
Facilities. We proposed to modify this
NWP to require pre-construction
notification for the construction or
expansion of stormwater management
facilities, but not for maintenance
activities. We also proposed to modify
the 300 linear foot limit for the loss of
stream bed by applying that limit to
ephemeral streams. We proposed to
allow district engineers to waive the 300
linear foot limit if the stream bed is
intermittent or ephemeral and the filling
and/or excavation of that stream bed
will result in minimal individual and
cumulative adverse effects on the
aquatic environment. In addition, we
proposed to remove the requirement for
prospective permittees to submit
maintenance plans and the permit text
requiring the submission of
compensatory mitigation proposals with
pre-construction notifications.
One commenter suggested we refer to
the definition of ‘‘stormwater
management facilities’’ rather than
furnish examples of the types of
stormwater management facilities in the
description of the NWP.
The text of the proposed NWP
describes the type and nature of
activities that are authorized in various
stormwater management facilities (e.g.,
construction, maintenance, excavation,
installation), rather than defining what
constitutes a stormwater management
facility. Therefore, we do not agree that
the language within the text of the NWP
is redundant or superfluous.
Several commenters requested we add
restrictions to this NWP to exclude its
use in special aquatic sites and/or
prohibit construction of in-stream
retention or detention basins and
construction of hardened channels (e.g.,
concrete or riprap).
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We do not agree it is necessary to
prohibit the construction of in-stream
retention or detention basins and/or
hardened channels since division
engineers can impose regional
conditions to this NWP to exclude
certain types of activities in specific
streams, watersheds, or other designated
aquatic resources to ensure impacts to
the aquatic environment are minimal,
individually and cumulatively. In
addition, since construction and
expansion activities require preconstruction notification, the district
engineer can either require case-specific
special conditions or exercise
discretionary authority to require an
individual permit if the proposed
activity, such as construction of instream basins and/or hardened
channels, would result in more than
minimal adverse impact on the aquatic
environment. All new construction and
expansion of existing facilities requires
a pre-construction notification.
Several commenters objected to the
application of a 300 linear foot
threshold for intermittent and
ephemeral streams, while other
commenters indicated the activities
authorized under this NWP should
apply exclusively to ephemeral streams
and prohibit work in intermittent and
perennial streams. One commenter
stated that no stormwater management
facilities should be constructed in
waters of the United States.
We agree that intermittent and
ephemeral streams often provide
important functions, services, and
values, although there are situations
where activities in these streams will
result only in minimal adverse effects
on the aquatic environment. In many
cases, the only practicable alternatives
involve constructing stormwater
management facilities in waters of the
United States. The pre-construction
notification process allows district
engineers to review proposed
construction and expansion activities on
a case-by-case basis to ensure that those
activities result in minimal individual
and cumulative adverse effects on the
aquatic environment.
In order for the 300 linear foot
threshold for intermittent and
ephemeral streams to be waived, the
district engineer must make a written
determination that the proposed work
will result in no more than minimal
adverse effects on the aquatic
environment. If the district engineer
does not provide written confirmation
of the waiver, then the 300 linear foot
limit remains in place and the
prospective permittee must obtain
another type of authorization for the
proposed activity. As an added level of
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protection, division engineers can
impose regional conditions to further
restrict or prohibit the use of NWP 43
in high value perennial, intermittent
and ephemeral streams. Please note that
this NWP prohibits discharges of
dredged or fill material to construct new
stormwater management facilities in
perennial streams.
Some commenters asserted that
activities authorized under this NWP
would result in adverse environmental
impacts on spawning habitat or cause
more than minimal adverse impacts to
the aquatic environment if the 300
linear foot limit is waived, and, as a
result should be evaluated under the
Corps individual permit process.
In general, we believe the activities
authorized under NWP 43 would result
in minimal adverse impacts to the
aquatic environment, including
spawning habitat. Requiring individual
permits for all activities that would
otherwise qualify for authorization
under NWP 43 based solely on the fact
that they involve the loss of greater than
300 linear feet of ephemeral or
intermittent stream bed would place an
unnecessary burden on the Corps and
the permittee, with negligible added
environmental benefits. District
engineers will use their knowledge of
the local aquatic environments and
case-specific circumstances to
determine when proposed activities
would result in more than minimal
adverse effects on the aquatic
environment and consequently require
an individual permit. In addition,
general conditions 2 and 3 provide for
the protection of aquatic life movement
and spawning habitat, respectively,
which collectively we believe will help
to ensure overall minimal impacts.
One of the commenters requested we
establish criteria for the district
engineer’s determination to waive the
300 linear foot limit. One other
commenter expressed concerns that in
the absence of such guidelines there
would be inconsistencies within the
Corps as to how or to what degree the
waiver is applied.
We believe deference must be given to
the district engineers’ expertise and
knowledge of the local aquatic
environment, as well as their
assessment of information submitted in
pre-construction notifications, to make
case-specific determinations on the
effects to the aquatic environment.
Based on the inherent variability across
the nation, we disagree that it is
necessary or appropriate to establish
nationally applicable criteria for the
application of the waiver. Aquatic
resource functions, services, and values
differ across the United States and,
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accordingly, there will be corresponding
differences in the criteria considered for
implementation of the waiver consistent
with regional and/or local variations.
District engineers will make their casespecific determinations on the
appropriateness of the waiver based on
the characteristics of the local aquatic
environment and in consideration of the
specific circumstances of the proposed
activity.
Some commenters suggested we
combine this NWP with NWP 3,
Maintenance, since both include
maintenance activities.
We believe the specific requirements
of NWP 43 are necessary to allow for
specific types of maintenance activities
that may not be authorized by NWP 3.
For example, NWP 43 authorizes
activities necessary to return the storm
water management facility to its original
design capacities, which may include
basins that are not considered structures
or fills. In contrast, NWP 3 is limited to
the repair, rehabilitation, or replacement
of structures or fills, or the removal of
accumulated sediments in the vicinity
of existing structures.
A few commenters requested we
provide clarifications to NWP 43,
including whether maintenance and
mitigation plans for these facilities
would be required. Several commenters
requested we retain the requirement for
submittal of maintenance plans for
stormwater management facilities. Other
commenters indicated the preconstruction notifications should
include maintenance plans, avoidance
and minimization measures, and water
quality management measures.
The removal of the requirement for
prospective permittees to submit
maintenance plans and compensatory
mitigation plans with pre-construction
notifications simplifies this NWP and
eliminates redundancy with general
condition 20, Mitigation. Maintenance
plans are not necessary if maintenance
does not increase the design capacity of
the facility. For new construction or
expansion of existing facilities,
compensatory mitigation requirements
are addressed in general condition 20,
Mitigation. Division engineers also have
the ability to impose regional conditions
to ensure specific activities authorized
under this NWP result in minimal
adverse impacts on the aquatic
environment.
One commenter indicated
maintenance of an existing stormwater
management facility should not require
Department of the Army authorization.
We disagree with this comment.
Unless an exempted activity, all work
and/or actions that result in the
discharge of dredged or fill material into
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waters of the United States require
Department of the Army authorization.
One commenter opposed the
elimination of the 1⁄10 acre preconstruction notification threshold.
We believe that pre-construction
notification should be required for all
new construction and expansion of
existing facilities in order for the Corps
to ensure that the individual and
cumulative adverse environmental
impacts associated with the project are
minimal.
One commenter indicated this NWP
should not apply to specific watersheds,
while another commenter insisted we
not re-issue this NWP.
We believe the stormwater
management facilities authorized under
NWP 43 often constitute vital
development or improvement projects
that serve important public functions,
including protection of aquatic
resources. While such activities may
need to be located in waters of the
United States, we believe the underlying
provisions of the NWP program that
require all authorized activities to have
minimal impacts on the aquatic
environment, coupled with the ability of
division engineers to impose regional
conditions on specific activities, will
provide effective regulatory mechanisms
for protecting the aquatic environment
without adding further restrictions on
the use of NWP 43.
One commenter indicated the
prohibition on use in non-tidal wetlands
adjacent to tidal waters is an unfair
limitation to prospective permittees in
coastal plains.
In consideration of the relatively high
functions, services, and values these
wetlands contribute to the overall health
of the aquatic environment on a national
basis, we do not agree that the
prohibition on the use of NWP 43 in
non-tidal wetlands adjacent to tidal
waters is unfair to those perspective
permittees located in coastal plains.
More importantly, this prohibition is
necessary to ensure that this NWP
authorize only activities with minimal
adverse effects, individually and
cumulatively.
We have slightly revised the wording
of this NWP to clarify that activities
which increase existing capacity may be
authorized as ‘‘expansion’’ of existing
facilities if pre-construction notification
is submitted.
This NWP is reissued as modified
above.
NWP 44. Mining Activities. We
proposed to simplify this NWP and
modify it to authorize all types of
mining activities except for coal mining.
Surface coal mining activities may be
authorized by NWP 21. Other types of
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coal mining activities may be authorized
by NWP 49 (Coal Remining Activities)
or NWP 50 (Underground Coal Mining
Activities). This NWP continues to
authorize aggregate mining and hard
rock/mineral mining activities. We
proposed to retain the 1⁄2 acre limit for
this NWP.
A number of commenters supported
reissuance of NWP 44, but opposed the
1⁄2 acre limit, stating that it is arbitrary
and duplicative of other existing
regulatory requirements, or is too
stringent for the permit to be useable.
Several commenters expressed support
for the 1⁄2-acre limit and recommended
adding a linear foot limit for stream
impacts. One commenter recommended
a 1⁄4 acre limit for this NWP, to protect
anadromous fish. One commenter
recommended a 2,000 linear foot limit
for impacts to streams.
We believe that the terms and
conditions of this NWP, including the
1⁄2-acre limit, will ensure that activities
authorized by this NWP result in no
more than minimal adverse effects to
the aquatic environment, individually
and cumulatively. Aggregate and hard
rock/mineral mining activities that do
not qualify for authorization under this
NWP can be authorized by individual
permits. We believe the 1⁄2 acre limit is
appropriate. We have modified the text
of this NWP to clarify that the 1⁄2 acre
limit applies to all non-tidal waters of
the United States. This NWP only
authorizes discharges of dredged or fill
material into certain non-tidal waters of
the United States. It does not authorize
discharges into tidal waters, or non-tidal
wetlands adjacent to tidal waters. As a
pre-construction notification must be
submitted for all activities, a specific
linear foot threshold for streams is not
necessary, as the district engineer can
exercise discretionary authority or
include special conditions to ensure
that impacts to streams are no more than
minimal. District or division engineers
can condition this NWP on a case-bycase or regional basis to protect
anadromous fish.
One commenter stated that ephemeral
streams, isolated waters, and artificially
created wetlands should not be
considered in the acreage limitations.
The acreage limit for this NWP
applies to waters of the United States.
Impacts to non-jurisdictional waters are
not considered as losses of waters of the
United States, and are not counted
towards the acreage limit for this NWP.
A couple of commenters stated that
the reclamation plan should not be
required as part of the pre-construction
notification. Pre-construction
notifications are frequently submitted to
the Corps before reclamation plans are
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required and the Corps has no authority
over mining reclamation.
The Corps needs to review the
reclamation plan to ensure that the
authorized activities, including any
required reclamation, do not result in
more than minimal adverse
environmental impact. In addition,
reclamation activities may affect the
need to require compensatory
mitigation.
Several commenters opposed the
removal of the prohibition on using
NWP 44 in 100-year floodplains, while
one commenter stated that certain
mining activities will increase the flood
storage capacity of floodplains and
streams and thereby reduce flooding,
which would benefit local communities.
In accordance with general condition
10, permittees must comply with
applicable state or local floodplain
management requirements that have
been approved by the Federal
Emergency Management Agency. In
addition, the Corps will address impacts
to 100-year floodplains through the
case-by-case review that occurs through
the pre-construction notification
process.
Several commenters supported the
simplification of NWP 44 by eliminating
redundant terms and conditions. One
commenter questioned whether the
permittee could mine the same area over
and over for aggregates as new deposits
accumulate each year. This commenter
also asked whether there is a limit on
the number of times or locations that the
permit can be used by one mining
company, what kind of separation is
necessary between mining sites, and
whether this NWP can be used by one
mining company on multiple streams.
This NWP can be used for any single
and complete mining activity that has
independent utility. The definitions of
‘‘single and complete project’’ and
‘‘independent utility’’ are provided in
the ‘‘Definitions’’ section. Therefore, it
is possible for an applicant to use this
NWP each year or on multiple sites,
provided each activity is a single and
complete project that complies with the
terms and conditions of the NWP,
including the requirement that the
individual and cumulative adverse
environmental impacts are minimal. In
response to pre-construction
notifications, district engineers will
determine whether proposed mining
activities constitute separate single and
complete projects that qualify for NWP
authorization.
A number of commenters were
opposed to the reissuance of NWP 44
because they believe the environmental
impacts associated with the permit are
more than minimal, and could result in
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significant adverse effects to rivers and
streams, including those with important
fish and mussel species. One
commenter stated that this NWP does
not satisfy the ‘‘similar in nature’’
requirement for general permits. One
commenter recommended that the
Corps establish an activity-specific NWP
for the aggregates industry. One
commenter recommended excluding
peat mining and in-stream gravel
mining, due to the environmental
damage produced by these types of
mining.
This NWP authorizes mining
activities that have no more than
minimal individual and cumulative
adverse effects on the aquatic
environment. The terms and conditions
of this NWP, including the NWP general
conditions, will ensure that these
mining activities will have no more than
minimal adverse environmental effects.
All activities authorized by this NWP
require pre-construction notification to
the district engineer prior to
commencement of mining activities.
The pre-construction notification
process allows district engineers to
review mining activities on a case-bycase basis, to ensure that the proposed
work has no more than minimal adverse
effects on the aquatic environment. The
district engineer can add special
conditions to the NWP authorization to
ensure that any adverse effects on the
aquatic environment are no more than
minimal, or exercise discretionary
authority to require an individual
permit for the work. This NWP complies
with the ‘‘similar in nature’’
requirement of general permits because
it authorizes a specific category of
activities (i.e., mining activities, except
for coal mining activities).
One commenter recommended that
the NWP be revoked in Montana
because these activities would have
more than minimal adverse
environmental effects. One commenter
also stated that the permit is not
adequately coordinated with state and
federal resource agencies and eliminates
the public interest review.
Division engineers may add regional
conditions to this NWP to enhance
protection of the aquatic environment
and address local concerns. Division
engineers can also revoke this NWP in
a specific geographic area if the use of
that NWP would result in more than
minimal adverse effects on the aquatic
environment, especially in high value or
unique wetlands and other waters.
This NWP is reissued with the
modification discussed above.
NWP 45. Repair of Uplands Damaged
by Discrete Events. This was proposed
as NWP A. We proposed to remove
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paragraph (iii) and portions of
paragraph (i) from NWP 3 to this new
NWP, to authorize emergency repair
activities. This was intended to simplify
NWP 3 and limit that NWP to routine
maintenance activities.
Numerous commenters supported the
issuance of this new NWP.
The majority of the comments
received in response to the proposed
NWP involved general concerns
regarding the way in which this permit
could affect time critical responses for
emergency situations. Many
commenters stated that authorization of
the repair, rehabilitation, or replacement
of structures or fills destroyed or
damaged by storms or other discrete
events should remain in NWP 3, since
NWP 3 did not require pre-construction
notification for those activities.
Therefore, NWP 3 would allow
expeditious maintenance activities,
especially for infrastructure and other
important features.
We agree, and have returned the
language to NWP 3 that authorizes the
repair, rehabilitation, or replacement of
structures or fills destroyed or damaged
by storms or other discrete events. We
wish to clarify that this NWP is not
intended to serve as an emergency
permit. An ‘‘emergency’’ is a situation
which would result in an unacceptable
hazard to life, a significant loss of
property, or an immediate, unforeseen,
and significant economic hardship if
corrective action is not undertaken
within a time period that does not allow
the Corps to process the application
under standard procedures. As many
commenters pointed out, pursuant to 33
CFR 325.2(e)(4), the Corps has already
developed special permitting and
permit application processing
procedures for emergency situations,
which are applicable to all types of DA
permits. Further, as several commenters
indicated, in accordance with 33 CFR
323.4(a)(2), certain emergency response
activities are exempted from the
permitting requirements of Section 404
of the Clean Water Act. As a result of
the changes discussed above, this NWP
authorizes only the restoration of
upland areas damaged by storms, floods,
or other discrete events. Those repairs
may or may not require emergency
processing, though in most cases we
believe they will not. We believe that
the confusion regarding the purpose of
this NWP was caused by the inclusion
of the word ‘‘Emergency’’ in its name.
In order to remove that confusion, we
are renaming this NWP ‘‘Repair of
Uplands Damaged by Discrete Events.’’
Several commenters expressed
concerns over the lack of clear limits for
this NWP, and recommended
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establishing acreage or linear-foot limits
in order to prevent more than minimal
impacts to the aquatic environment. On
the other hand, several commenters
suggested establishing thresholds that
would require pre-construction
notification only for large-scale
activities. One commenter asked how
‘‘pre-event’’ bottom contours of
waterbodies would be determined,
particularly on those sites with limited
or no data, aerial photos, or other
information.
This NWP only authorizes the
restoration of damaged uplands to the
extent that existed before the damage
occurred, along with any bank
stabilization necessary to protect the
restored uplands. This NWP may also
authorize minor dredging where
necessary to restore material that has
washed from the uplands into a
neighboring waterbody. Since this NWP
only authorizes activities to restore
damaged areas to previously existing
conditions, we do not believe that it will
result in adverse effects that did not
previously exist. We believe that the
pre-construction notification
requirements established for this NWP
are necessary to ensure that the
proposed activities will result in no
more than minimal adverse effects. We
recognize that the pre-construction
notification requirement imposes an
additional burden on project
proponents, but we do not believe that
it is inequitable or, in most
circumstances, substantial. The district
engineer has discretionary authority to
require an individual permit for any
proposed activity that will have more
than minimal individual or cumulative
adverse effects on the environment, and
the pre-construction notification
requirement is necessary for the
effective use of this authority. When
reviewing pre-construction
notifications, district engineers will use
available information, including
documentation provided by permit
applicants in accordance with the
‘‘Notification’’ provision of this NWP, to
determine the pre-existing conditions. If
maps or photographs are not available,
the district engineer’s judgment will be
used.
One commenter stated that this NWP
could interfere with tribal rights,
including treaty fishing access, and that
it could severely impact anadromous
salmonid habitat.
District engineers can impose special
conditions or assert discretionary
authority and require an individual
permit for projects that have more than
minimal adverse effect on the aquatic
environment or other public interest
factors. Furthermore, activities
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authorized under this NWP must
comply with the NWP general
conditions, including general condition
16, Tribal Rights, and general condition
2, Aquatic Life Movements.
One commenter requested
clarification regarding the effects of
changes in the ordinary high water mark
after discrete storm or flood events on
the scope of activities authorized under
this NWP.
Discrete storm or flood events may
result in erosion, which can change the
ordinary high water mark (OHWM) in
non-tidal waters or high tide line (HTL)
in tidal waters. For the purposes of this
NWP, determinations regarding the
location of the OHWM or HTL will be
made by the district engineer upon
receipt of the pre-construction
notification.
One commenter stated that this NWP
is unnecessary since repair activities
that do not exceed the original scope of
the project should be covered by the
original authorization. One commenter
stated that the Corps should not allow
rebuilding of structures located in
floodplains which are likely to be
damaged again by subsequent storm
events.
This NWP authorizes the restoration
of uplands damaged by a discrete event,
in cases where there is no available
authorization to restore those areas.
There would be no original
authorization for natural uplands that
were damaged by a discrete event. Manmade uplands may have been
constructed without the need to obtain
a Department of the Army permit.
Activities authorized by NWP must
comply with general condition 10, Fills
within 100-year Floodplains, which
requires all NWP activities to comply
with any applicable FEMA-approved
state or local floodplain management
requirements. We do not agree that there
should be a prohibition against
rebuilding structures in floodplains.
Such decisions should be made by the
appropriate state or local authorities, in
accordance with FEMA-approved
floodplain management requirements.
A number of commenters stated that
the terms of the NWP were
contradictory with regards to the start
date of the authorized activity. These
commenters requested clarification as to
whether the work must commence
within two years from the date of the
damages or from the date the preconstruction notification is filed.
We have modified the text of this
NWP to clarify that activities authorized
by this permit must commence, or be
under contract to commence, within
two years of the date of damage. This
change will make the second paragraph
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of this NWP consistent with the preconstruction notification requirements
for this NWP. This requirement may be
waived by the district engineer if the
permittee can show that delays were
unavoidable.
One commenter indicated that this
NWP should also authorize temporary
impacts that are necessary to repair or
provide maintenance to damaged
structures.
This NWP does not authorize
temporary fills, structures, or work
required to conduct the upland
restoration activities. Those temporary
activities may be authorized by NWP 33.
Proposed NWP A is issued as NWP
45, with the modifications discussed
above.
NWP 46. Discharges in Ditches. This
NWP was proposed as NWP B to
authorize discharges of dredged or fill
material into certain types of ditches
and canals. This NWP allows a
landowner to return his or her land to
its prior condition, but only in those
cases where the ditches or canals meet
all four criteria specified in the NWP.
To qualify for this NWP, those ditches
and canals must: (1) Be constructed in
uplands, (2) receive water from another
water of the United States, (3) divert
water to another water of the United
States, and (4) be determined to be
waters of the United States. These four
criteria will limit the use of this NWP
to those ditches and canals that
generally provide few aquatic resource
functions. This proposed NWP does not
authorize discharges of dredged or fill
material into ditches or canals that were
constructed in waters of the United
States, such as streams.
Several commenters supported the
new NWP. Several commenters stated
that the limits for this NWP are too high
to prevent more than minimal impacts
on the aquatic ecosystem, particularly to
flood storage and water quality. Several
commenters recommended establishing
a 300 linear foot threshold for preconstruction notification and a 1⁄2 acre
limit on permitted impacts, in order to
be consistent with other NWPs. Another
commenter stated that filling ditches
should not be allowed without an
assessment of how the hydrology was
altered when the ditch was created and
how the hydrology and water quality
would be affected if it is filled. Another
commenter recommended requiring preconstruction notification for all
activities under this NWP, because
authorized activities could result in
isolating wetlands that are adjacent to
the ditches and severing the migratory
pathways of aquatic organisms. On the
other hand, one commenter stated that
since the ditches regulated by this
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permit have been determined to provide
few aquatic resource functions, the
thresholds for pre-construction
notification and limits for permitted
impacts should be increased. Similarly,
one commenter suggested that this NWP
should not have any limits, because the
regulated ditches are not natural.
This NWP authorizes discharges of
dredged or fill material into certain
types of ditches. Those ditches must
meet all of the criteria listed in the first
paragraph of the NWP. To ensure that
this NWP is used only to authorize
discharges into those types of ditches,
and to ensure that those activities result
in minimal adverse effects on the
aquatic environment, we are requiring
pre-construction notification for all
activities. To address concerns
regarding the jurisdictional status of the
waters of the United States other than
the ditch to be filled, we have changed
the text of this NWP to state that those
other waters had to have been waters of
the United States prior to the
construction of the ditch. Therefore, the
jurisdictional status of those waters
should remain unchanged after the
ditch is filled.
We are retaining the proposed one
acre limit for this NWP. We believe that
the applicable provisions and terms and
conditions, including the general
conditions, the pre-construction
notification requirements, and the
ability of division and district engineers
to assert discretionary authority and
impose regional and case-specific
conditions on this NWP, will ensure
that the activities authorized will result
in no more than minimal individual and
cumulative adverse effects on the
aquatic environment.
One commenter stated that a
determination of absence or presence of
salmonids should be required in
channels potentially accessible by
anadromous salmonids. Another
commenter said that this NWP should
not authorize discharges of dredged or
fill material into streams.
Potential impacts to salmon species
will be considered by district engineers
during the review of pre-construction
notifications. General condition 2,
Aquatic Life Movements, prohibits
activities which could disrupt the
necessary life cycle movements of
aquatic species. If deemed appropriated,
this NWP can be regionally conditioned
by division engineers to limit or restrict
the use of this NWP in waters accessible
to anadromous salmonid species. The
text of this NWP clearly states that it
does not authorize discharges into
streams, or streams that have been
relocated into uplands.
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Several commenters stated that the
proposed NWP is contrary to Section
404(e) of the Clean Water Act because
it is not a general permit for a category
of activities that are similar in nature
but rather a permit for a category of
waters, and that the Corps has no
authority to issue a permit for a category
of waters. One commenter suggested
that the Corps clarify that the NWP is
not limited to situations where the
landowner seeks to return his or her
land to its prior condition. One
commenter requested clarification on
whether impacts to roadside ditches for
road improvements can be permitted
under this NWP, or if NWP 14 would be
applicable. Similarly, another
commenter suggested that fill for access
roads should be included in this NWP.
We expect that this NWP will be
mostly used by landowners to return
ditches or portions of ditches to their
prior upland condition. However, this
NWP may also authorize ditch
relocation and reshaping activities. To
help ensure that this NWP only
authorizes activities with minimal
individual and cumulative adverse
effects on the aquatic environment, we
have added language stating that this
NWP does not authorize discharges of
dredged or fill material that will
increase the drainage capacity of the
ditch and will drain other waters of the
United States. In the event that the ditch
is returned to its prior upland condition,
the Corps would no longer have
regulatory jurisdiction over that ditch.
This NWP may authorize discharges of
dredged or fill material into roadside
ditches, provided those ditches meet all
four criteria specified in the first
paragraph of this NWP. Access roads
may be authorized by other NWPs,
regional general permits, or individual
permits.
One commenter requested
clarification as to whether all four or
only one of the four eligibility criteria
are needed for a project to be authorized
under this NWP. The same commenter
requested clarification on the eligibility
criterion ‘‘receive water from another
waters of the United States.’’ One
commenter asked whether this NWP
could be used to authorize discharges of
dredged or fill material into both tidal
and non-tidal waters of the United
States. One commenter said that this
NWP should not authorize discharges
into canals, because canals can be large
aquatic systems and the adverse
environmental effects could be more
than minimal.
This NWP applies only to those
ditches that meet all four criteria
specified in the first paragraph of the
NWP. The second criterion for eligible
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ditches refers to situations where the
ditch constructed in uplands receives
surface water flow from another water of
the United States that existed prior to
the construction of that upland ditch.
To ensure that this NWP authorizes
only those activities with minimal
individual and cumulative adverse
effects on the aquatic environment, we
have limited this NWP to discharges of
dredged or fill material into non-tidal
ditches. In addition, it does not
authorize discharges of dredged or fill
material into navigable waters of the
United States (i.e., section 10 waters).
We have removed the word ‘‘canal’’
from this NWP, to provide further
clarity since canals may be navigable
waters of the United States. Discharges
into a non-tidal ditch that flows into a
tidal water could be covered under
NWP 46, but not discharges into a
‘‘tidal’’ ditch, i.e., one into which tidal
waters flow.
A number of commenters questioned
or requested clarification of Corps
jurisdiction over ditches following the
Supreme Court decisions in Rapanos
and Carabell. One commenter requested
clarification on whether the term ‘‘water
of the United States’’ includes wetlands
or only waterbodies, and whether a
ditch connecting two wetlands would
qualify for authorization under this
NWP. One commenter suggested
providing guidelines for or examples of
the information required to determine
that a ditch was constructed in uplands.
This NWP can be used to authorize
discharges of dredged or fill material
into ditches that meet the four criteria
in the first paragraph, as well as the
other terms and conditions of this NWP.
The waters of the United States other
than the ditch constructed in uplands
may consist of wetlands, open waters, or
both. This preamble does not address
the limits of jurisdiction after Rapanos
and Carabell.
Data used to determine whether a
ditch was constructed in uplands may
be obtained from a variety of sources,
such as aerial photographs, soil surveys,
property maps, plans, plots or plats,
previous jurisdictional determinations
and data sheets, topographical maps,
wetland inventory maps, and
photographs.
One commenter stated that mitigation
should be required for impacts to
wetlands and aquatic life that may be
established in those ditches. In contrast,
another commenter stated that requiring
mitigation for reversion to a prior
upland condition is excessive and
unreasonable.
We do not believe that it would be
appropriate or practical to establish a
national standard requiring mitigation
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for all activities authorized by this
NWP. The need for compensatory
mitigation to ensure minimal individual
and cumulative adverse effects will be
made by district engineers on a case-bycase basis, in response to preconstruction notifications. We believe
that the provisions of general conditions
27 and 20 will allow the district
engineer to determine if any
compensatory mitigation is needed to
reduce the effects of the activities
authorized under this permit to the
minimal level.
One commenter suggested that the
one-acre limit should not apply if the
impacted ditch is replaced with another
ditch that would perform the same
functions.
Although this NWP may be used to
authorize discharges of dredged or fill
material into ditches for the purpose of
relocating those ditches, the one acre
limit applies to the loss of waters of the
United States that results from the
discharge of dredged or fill material into
the existing ditch.
One commenter requested
clarification on how the ‘‘constructed in
uplands’’ criterion reconciles with
Corps policy at 51 FR 41217, under
which ditches excavated on dry land are
generally not waters of the United
States.
The proposed NWP is consistent with
the policy established in the November
13, 1986 Federal Register Notice (51 FR
41217), because that policy also states
that the Corps reserves the right on a
case-by-case basis to determine whether
non-tidal ditches excavated on dry land
or other features constitute waters of the
United States.
One commenter requested
clarification on how this NWP
reconciles with the Section 404
exemption for construction and
maintenance of irrigation ditches at 33
CFR 323.4(a)(3).
The Section 404 exemption at 33 CFR
323.4(a)(3) applies to construction and
maintenance of irrigation ditches or the
maintenance of drainage ditches. This
NWP authorizes activities not covered
in the exemption, such as discharges of
dredged or fill material to restore the
area to its previous upland condition.
One commenter stated that this NWP
should not be issued because it is
contrary to the Congressional intention
that ditches should be regulated as point
sources and not as navigable waters.
This preamble does not address the
limits of Clean Water Act jurisdiction.
To the extent that ditches are
determined to be waters of the United
States, this permit provides
authorization for discharges of dredged
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or fill material into them provided all
conditions for its use are met.
One commenter recommended
providing definitions for ‘‘ditch’’ and
‘‘canal’’.
We believe that district engineers
should maintain the discretion to
determine on a case-by-case basis
whether particular features are ditches
or canals and also are waters of the
United States.
Proposed NWP B is issued as NWP 46
with the modifications discussed above.
NWP 47. Pipeline Safety Program
Designated Time Sensitive Inspections
and Repairs. In the September 26, 2006,
Federal Register notice, we proposed
this NWP (as proposed NWP C) to
authorize the inspection, repair,
rehabilitation, or replacement of any
currently serviceable structure or fill for
pipelines that are determined to be
time-sensitive in accordance with the
Pipeline and Hazardous Materials Safety
Administration’s Pipeline Safety
Program (PHP), including its criteria at
49 CFR parts 192 and 195.
Thirteen comment letters were
received concerning this proposed NWP
with six expressing strong support for
its issuance but also inquiring about the
applicability of general conditions 17
(Endangered Species) and 18 (Historic
Properties) to the use of the permit. Six
commenters recommended that the
Corps enter into programmatic ESA
consultation with PHP and the U.S. Fish
and Wildlife Service and the National
Marine Fisheries Service.
This NWP only authorizes activities
that are included in the U.S. Department
of Transportation’s Pipeline Repair and
Environmental Guidance System
(PREGS). The PHP is the lead Federal
agency for these activities and, as such,
conducts any Section 7 consultation
required under the Endangered Species
Act and consultation required under
Section 106 of the National Historic
Preservation Act. In cases where PHP
has not conducted consultation required
by either Section 7 of the Endangered
Species Act, or Section 106 of the
National Historic Preservation Act,
permittees are required by 33 CFR
330.4(f) and (g) to notify the Corps if
there are threatened or endangered
species or critical habitat, or historic
properties that might be affected or are
in the vicinity of the project.
One commenter declared that
‘‘inspections’’ should be removed from
the list of authorized activities since
technology exists which allows pipeline
operators to evaluate a pipeline without
the need to visually inspect it. One
commenter said that this NWP should
not authorize the repair of pipelines that
have deteriorated as a result of neglect.
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Two commenters stated that acreage
limits should be placed on the NWP.
One commenter remarked that access
roads should be authorized by the NWP
because problems will occur when an
activity requires use of multiple NWPs
and one of the other NWPs has an
acreage limit.
We disagree with the first two
comments of the preceding paragraph.
Pipeline inspections are critical
activities related to the repair of these
pipelines. In certain instances it is
necessary that the pipeline be visually
inspected, and this permit allows
excavation to expose the pipeline.
Impacts authorized under this NWP will
be temporary in nature so the aquatic
resources will recover over time. This
NWP provides Department of the Army
authorization for the repair,
rehabilitation, or replacement of
currently serviceable pipelines. These
pipelines are unlikely to become
unserviceable as a result of neglect,
since operators are required to
periodically inspect these pipelines and
make necessary repairs or replacements.
We do not believe acreage limits are
necessary, given the nature of the
category of activities authorized by this
NWP. Access roads will not generally
need to be constructed to conduct the
pipeline inspection and repair, since
access roads would likely have been
built at the time the pipeline was
constructed, or the terrain will not
impede access to the pipeline. If
temporary access roads are necessary to
conduct the pipeline inspection and
repair activity, they are authorized by
this NWP as long as they are removed
upon completion of the work. This NWP
requires that all temporary structures
and fill be removed and the area
restored to preconstruction elevations.
We have modified paragraph (c) of this
NWP so that it is consistent with general
condition 13, Removal of Temporary
Fills.
One commenter inquired as to why
temporary activities are included in the
proposed NWP when this work is being
removed from other NWPs that
authorize maintenance. Two
commenters requested we add a preconstruction notification requirement
for environmentally sensitive areas. One
commenter said the pre-construction
notification should be required for all
activities. Two commenters were against
and one commenter supported
prohibiting division engineers from
placing regional conditions on the NWP.
Since the objective of this NWP is to
authorize inspections and repairs for
eligible pipelines in a timely manner,
the NWP authorizes temporary activities
necessary to conduct the inspection,
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repair, rehabilitation, or replacement
activity. We do not agree that it is
necessary to require pre-construction
notification for these activities, since
PHP is the lead Federal agency for these
activities. Submitting a pre-construction
notification when a pipeline is in
critical need for repair will delay the
repair and increase the risk that the
pipeline will leak and cause more
damage to the aquatic environment,
particularly environmentally sensitive
areas. Given the nature of the activities
authorized by this NWP, as well as its
objective of authorizing these activities
in a timely manner, we believe it is
unnecessary for division engineers to
regionally condition this NWP.
However, division engineers can impose
regional conditions on this NWP that
are limited to measures necessary to
minimize adverse effects to the aquatic
environment, as long as those regional
conditions do not require preconstruction notification or cause delays
to inspection and repair activities. We
have added a ‘‘Note’’ to this NWP to
explain what types of regional
conditions may be added by division
engineers.
Two commenters suggested that in
order for water quality certifications to
be issued, a list of ‘‘time-sensitive’’
activities as well as appropriate best
management practices must be provided
by PHP and an opportunity for public
comment should be given for the best
management practices. One commenter
stated PHP has not made all the best
management practices available to the
pipeline operators yet.
We do not agree that it is either
necessary or feasible to provide a list of
time-sensitive activities or best
management practices for states, Indian
tribes, and EPA to make their water
quality certification decisions for this
NWP. In response to concerns raised by
states or tribes through the water quality
certification process, districts may add
regional conditions as long as they do
not preclude its use for time sensitive
repairs. Identification of time-sensitive
activities will be made in the future, as
the program is implemented. Best
management practices may vary by
region, and we do not believe it is
necessary for PHP to solicit public
comment on those best management
practices prior to implementing this
NWP.
Proposed NWP C is issued as NWP 47
with the modifications discussed above.
NWP 48. Existing Commercial
Shellfish Aquaculture Activities. We
proposed to issue this new NWP to
authorize ongoing shellfish aquaculture
activities throughout the United States.
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The majority of commenters
expressed their support for this new
NWP, stating that existing commercial
shellfish operations do not have more
than minimal adverse impacts on the
aquatic environment and contribute
benefits to the ecosystem that balance
any adverse impact. Referencing
numerous scientific studies as evidence
of the beneficial aspects of shellfish
culture, many of these commenters
expressed their desire for the 25-acre
threshold for pre-construction
notification to be raised considerably, or
eliminated entirely, stating it was
arbitrary and created an unnecessary
bureaucratic paperwork burden for the
operators and the Corps. In addition,
many commenters recommended that
the NWP not be limited only to existing
operations but also be available for the
expansion of existing operations and for
new operations. One commenter
supported limiting this NWP to existing
operations. A few commenters objected
to the issuance of this NWP, stating that
commercial shellfish aquaculture
operations of unlimited size threaten
submerged aquatic vegetation,
shorebirds, and other estuarine
resources, and potentially exceed the
minimal impact threshold, both
individually and cumulatively. Several
commenters believed that potential for
adverse impacts was related more to
specific activities than to the geographic
extent of an operation, and that whether
an operation engaged in these activities
was thus a better basis for limits or preconstruction notification thresholds.
One commenter recommended requiring
pre-construction notification for the use
of canopy predator nets that cover broad
areas of an aquaculture operation
because of potential impacts to a variety
of aquatic species. One commenter
recommended requiring preconstruction notification for all
activities authorized by this NWP, while
another commenter suggested a simple
reporting requirement in lieu of a preconstruction notification.
Since shellfish improve water quality
and increase food production, we
believe that there is generally a net
increase in aquatic resource functions in
estuaries or bays where shellfish are
produced. We do not believe it is
necessary to require pre-construction
notification for all activities authorized
by this NWP, including those that
involve canopy predator nets. Concerns
regarding the use of canopy predator
nets are more appropriately address
through regional conditions imposed by
division engineers, or by special
conditions added to NWP
authorizations by district engineers.
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After review of the comments and of
scientific literature, we have modified
the pre-construction notification
requirements. Pre-construction
notification will be required if the
project area is greater than 100 acres or
if the operation conducts any of the
following activities: any reconfiguration
of the aquaculture activity, such as
relocating existing operations into
portions of the project area not
previously used for aquaculture
activities; a change in species being
cultivated; a change in culture methods
(e.g., from bottom culture to off-bottom
culture); or dredge harvesting, tilling, or
harrowing in areas inhabited by
submerged aquatic vegetation. We do
not believe it is necessary to require preconstruction notification for on-going
operations, unless the project area is
greater than 100 acres or the operation
involves dredge harvesting, tilling, or
harrowing in areas inhabited by
submerged aquatic vegetation, since ongoing operations not meeting these
criteria are unlikely to result in
significant adverse environmental
effects. However, in order to generate
better information for future permitting
decisions, for those activities that do not
require pre-construction notification, we
are requiring operators to submit a brief
report that will provide the district
engineer with basic information on the
activity. The report must include the
size of the project area, the location of
the aquaculture operations, a brief
description of the culture methods used,
a brief description of the harvesting
method(s) used, the name(s) of the
cultivated species, and a statement
addressing whether canopy predator
nets will be used. For each existing
operation not submitting a preconstruction notification, the report
needs to be submitted within 90 days of
the effective date of this NWP.
Following submission of this one-time
report, no further reporting is necessary.
However, if there are any changes to the
operation that require Department of the
Army (DA) authorization, then preconstruction notification is required if
the proposed changes meet any of the
pre-construction notification triggers.
Depending on the region and culture
method used, there may be additional
restrictions (e.g., limits on timing of
certain activities) that are necessary to
further minimize impacts to aquatic
resources. These regional concerns are
best addressed by district engineers in
coordination with State and local
agencies and handled through regional
conditioning.
Many commenters were confused
about the definitions of ‘‘existing
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operation’’ and ‘‘project area’’ and
requested clarification of these terms.
For the purposes of this NWP, an
existing operation is one that has been
granted a permit, license, or lease from
a state or local agency specifically
authorizing commercial aquaculture
activities and which has undertaken
such activities prior to the date of
issuance of this NWP. For the purposes
of this NWP, the project area is defined
as the area of waters of the United States
occupied by the existing operation. In
most cases, the project area will consist
of the area covered by the state or local
aquaculture permit, license, or lease.
The project area may consist of several
sites that are not contiguous. The project
area may include areas in which there
has been no previous aquaculture
activity and/or areas that periodically
are allowed to lie fallow as part of
normal operations. Relocation of
existing operations into portions of the
project area not previously used for
aquaculture activities may be authorized
by this NWP but will require a preconstruction notification. Cultivation in
areas that were previously used but
allowed to lie fallow does not require a
pre-construction notification. Operators
should maintain appropriate
documentation showing which areas
were previously cultivated.
This NWP is limited to work
associated with the continued operation
of existing commercial shellfish
operations, many of which have been in
place for hundreds of years. The
potential for adverse environmental
impacts from such existing operations is
minimal, and we support the objectives
of the U.S. Department of Commerce’s
Aquaculture Policy to increase shellfish
productivity in this country. Although
we believe new projects and the
expansion of existing operations are also
unlikely to have a high potential for
adverse affects on the aquatic
environment, without an established
data set from which to work, we are not
prepared to include them in this NWP
at this time. Although new projects and
the expansion of existing operations are
not authorized initially by this NWP,
once authorized by another form of DA
permit, such as a regional general
permit or an individual permit, the
commercial shellfish activities may
continue in accordance with the terms
and conditions of the issued permit
and/or this NWP. Division engineers
will conduct regional reviews of
commercial shellfish aquaculture
activities in coordination with
interested agencies and shellfish
producers over the next 5 years. After
these reviews are completed, we may be
prepared to propose an NWP to
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authorize new commercial shellfish
aquaculture operations and the
expansion of existing operations in the
next NWP re-issuance cycle. The
information gathered through the preconstruction notification process and
reporting requirement for existing
operations in the current NWP will
support this effort.
Several commenters expressed
confusion regarding whether ongoing
commercial shellfish operations require
reauthorization under this NWP, if those
existing operations have previously
been permitted by the Corps.
Existing operations previously
authorized by another NWP or another
form of DA permit, such as a regional
general permit or an individual permit,
are covered until the expiration of the
original permit. If the operator wishes to
continue, and the operation’s size,
conditions, and/or practices trigger the
pre-construction notification
requirements of this NWP, then a preconstruction notification must be
submitted to the appropriate district
office for review prior to the expiration
date of the original permit in order to
remain in compliance with Federal
laws. If the pre-construction notification
requirements are not triggered, the
operator must submit the required brief
report within 90 days of the beginning
of coverage under this NWP.
This NWP authorizes the continued
operation of existing commercial
shellfish aquaculture operations. The
continued operation of an aquaculture
activity may involve removing and
replacing structures in navigable waters
of the United States on a recurring basis
and requires a current DA permit.
However, if an operator is installing a
fixed structure, the construction period
for a DA permit is the period of time
where the permittee is authorized to
conduct work in navigable waters of the
United States and/or discharge dredged
or fill material into waters of the United
States. Once the DA permit expires,
further authorization is not required to
maintain the structures or fills, but if
additional work in navigable waters or
discharges of dredged or fill material in
jurisdictional waters are necessary for
the continued operation of those
activities, then another DA permit is
required.
Many commenters were confused
about the requirement to submit a preconstruction notification, assuming that
having to submit a pre-construction
notification meant that an individual
permit would be required. The
requirement to submit a preconstruction notification does not mean
that an individual permit will be
required. Instead, it means that a district
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office will review the project, in
coordination with appropriate resource
agencies, within a 45-day timeframe and
respond to the applicant with either a
verification of the applicability of the
NWP or a determination that an
individual permit, or other type of DA
permit, is required. If the applicant does
not hear back from the Corps within 45
days, he or she may assume that the
operation is authorized by the NWP.
A pre-construction notification is a
brief document that is intended to
provide the district engineer with
enough information to determine
whether an activity is authorized by
NWP. The information requirements for
a pre-construction notification are listed
in paragraph (b) of general condition 27,
Pre-Construction Notification. Detailed
studies or analyses are not required for
pre-construction notifications. The
required description of the direct and
indirect adverse environmental effects
that are expected to result from the
NWP activity should be brief, but with
sufficient detail to allow the district
engineer to determine whether the
adverse environmental effects will be
minimal and assess the need for
compensatory mitigation. The
description for the pre-construction
notification should include the size of
the project area, the name(s) of the
species being cultivated, the types of
cultivation methods (e.g., long lines,
bottom culture, rack and bags), and the
harvesting method (e.g., hand pick,
dredge, long line harvest). The
description should also state when
dredge harvesting, harrowing, or tilling
will occur in waters with SAV.
For all projects that do not trigger the
pre-construction notification
requirements of the NWP, submission of
a brief report is required. This reporting
requirement will help us monitor the
use of this NWP, to help ensure that it
authorizes only those activities that
have minimal individual and
cumulative adverse effects on the
aquatic environment and other public
interest review factors. We have
attempted to keep the reporting
requirement as simple as possible, to
minimize administrative burdens on
operators.
A few commenters suggested that
NWP 48 is unnecessary because NWPs
4 and 27 adequately cover all the needs
of commercial shellfish operations.
Although shellfish seeding activities
were authorized by previous versions of
NWP 4, that NWP did not authorize
additional structures or work in
navigable waters commonly associated
with commercial shellfish aquaculture
activities, such as the installation of
stakes and netting in navigable waters to
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prevent predators from feeding upon the
shellfish. Because of the issuance of this
NWP and the modification of NWP 27,
it is no longer necessary to include
shellfish seeding in the list of activities
authorized by NWP 4 and we have
removed it. NWP 27 does not cover
commercial shellfish operations. It
covers shellfish habitat restoration
activities, including shellfish seeding,
that are conducted to restore shellfish
populations. Restored populations may,
at some future date, be subject to
recreational harvesting; but the purpose
of activities conducted under NWP 27 is
restoration, not commercial aquaculture.
Although NWP 48 represents a change
in how commercial shellfishing
operations are being regulated by the
Corps, structures and other work in
navigable waters of the United States
have been regulated activities for
decades. Discharges of dredged or fill
material into waters of the United States
have been regulated under Section 404
of the Clean Water Act since 1972, but
the definitions of these terms have
changed over the years. Individual
permits remain a permitting tool that
will be necessary in some
circumstances. There are several
districts that currently have regional
general permits in place to authorize
aquaculture activities and more general
permits are expected to be developed.
In the preamble to the September 26,
2006, proposal, we solicited comments
on whether to impose limits on the
quantity of dredged or fill material that
could be discharged into navigable
waters under this NWP. One commenter
said that this NWP should be
conditioned to prohibit discharges of
dredged or fill material or to require preconstruction notification for each
activity involving such discharges.
Many commenters stated that there
should be no limitation on the quantity
of dredged or fill material that could be
discharged into navigable waters
because the cost of such material is
limiting and also because most of the
material is removed during harvest.
Many mentioned large Federal
restoration projects that have utilized
shellfish seeding methods to enhance
estuaries. Several commenters objected
to having no limits and several
suggested limiting the discharge to 3 to
6 inches or a certain percentage of the
water column. Several others indicated
that materials such as marl, concrete,
and gravel, in addition to shell and shell
fragments, should be included in the
material authorized for discharge.
It would be illogical to prohibit
discharges of dredged or fill material
under this permit, since without such
discharges, no permit is required
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anyway. This NWP authorizes
discharges of dredged or fill material
into waters of the United States only for
shellfish seeding, rearing, cultivating,
transplanting, and harvesting activities
for on-going commercial shellfish
aquaculture activities. With the
exception of harvesting activities, such
discharges usually enhance habitat
characteristics to support the growth of
shellfish. As for harvesting activities,
pre-construction notification is required
for dredge harvesting in areas inhabited
by submerged aquatic vegetation, so
case-by-case review will be conducted
to determine if the activity results in
more than minimal adverse effects on
the aquatic environment. Preconstruction notification is also
required for tilling and harrowing in
submerged aquatic vegetation. Other
harvesting activities that are part of ongoing activities are unlikely to result in
more than minimal adverse effects.
Division engineers may impose regional
conditions on this NWP to further
restrict cultivation or harvesting
practices or to require pre-construction
notification for additional practices that
may be of concern within a particular
area.
Many commenters expressed concern
over whether the gear associated with
commercial shellfish culture would be
authorized by this NWP, noting that
much of the in-water gear serves as
habitat for other aquatic species and is
necessary for the success of a
commercial shellfish venture. Other
commenters expressed concern over the
waste and trash left by geoduck
operations and the adverse impacts that
litter has on the surrounding intertidal
environment.
This NWP authorizes structures or
work in navigable waters of the United
States, as well as discharges of dredged
or fill material into all waters of the
United States for the purposes of the
commercial seeding, rearing,
cultivating, transplanting, and
harvesting of shellfish, which may
involve the installation of buoys, floats,
racks, trays, nets, lines, tubes, and
containers, as well as other associated
structures and work. The language of
the NWP has been modified to clarify
that it does not authorize the discharge
of dredged or fill material into waters of
the United States for attendant features
of commercial aquaculture operations
such as boat ramps, stockpiles, staging
areas, and moorings or for the
deposition of shell material back into
tidal waters as a waste material. As
stated above, discharges of dredged or
fill material below the high tide line/
ordinary high water mark must be of the
minimum necessary to provide suitable
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planting substrate. Examples of
commercial shellfish species for which
this NWP may be used to authorize
existing commercial aquaculture
activities include oysters, clams,
geoducks, mussels, and scallops. The
proposed NWP does not authorize
commercial aquaculture activities for
crustaceans or finfish. Types of gear
specific to a particular region or species
are best evaluated on a regional basis by
the district engineer and can be
addressed through regional conditions.
There are different types of shellfish
seed that can be used to increase
shellfish production. Shellfish seed may
consist of immature individual
shellfish, an individual shellfish
attached to a shell or shell fragment (i.e.,
spat on shell) and shellfish shells, shell
fragments, and/or shell fragments mixed
with gravel/concrete/limestone placed
into waters to provide a substrate for
attachment by free swimming shellfish
larvae (i.e., natural catch). Several
commenters asked that we clarify the
definition of shellfish seeding. We have
provided a definition of shellfish
seeding in the ‘‘Definitions’’ section of
the NWPs. This definition was based on
the definition provided in the preamble
to the September 26, 2006, Federal
Register notice (71 FR 56275).
Most commenters asked that we
clarify our definition of submerged
aquatic vegetation (SAV) and asked that
we limit our concern to those species of
aquatic vegetation that have been shown
to have beneficial environmental effects.
Some commenters expressed concern
that any commercial aquaculture
activity would have a negative impact
on SAV and therefore this NWP should
not be issued. Many commenters asked
that we remove the pre-construction
notification requirement for operations
having more than 10 acres of the project
area occupied by SAV, stating that
shellfish beds clarify the water thereby
increasing the likelihood that SAV
would colonize their project area. A few
commenters suggested that we define
the density of bed and length of time
present (i.e., recognize seasonal
population fluctuation) necessary to
trigger the reporting requirement.
Commercial shellfish aquaculture
activities often take place in, and are
found to co-exist with, intertidal areas
that are occupied by submerged aquatic
vegetation (i.e., vegetated shallows). The
definition of vegetated shallows (see
Part D, Definitions) clarifies that
vegetated shallows are those areas that
are permanently inundated and under
normal circumstances have rooted
aquatic vegetation, such as seagrasses in
marine and estuarine systems and a
variety of vascular rooted plants in
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freshwater systems. Macroalgae are not
included in our definition of SAV nor
is it our intent to provide protection for
noxious or invasive species such as
Zostera japonica. However, to minimize
adverse effects to valuable aquatic
habitat, such as shallows vegetated by
species such as Zostera marina, we are
requiring pre-construction notification
for dredge harvesting, tilling, or
harrowing in areas inhabited by SAV.
To capture the regional variances, such
as colonization rate, population shifts,
density, and species composition,
districts may choose to further refine the
definition of SAV in their regional
conditions to better reflect
environmental circumstances in their
region. We are removing the proposed
requirement to submit a preconstruction notification if the project
area includes 10 acres or more of SAV
because we have determined that only
certain types of activities (dredge
harvesting, tilling, harrowing) in SAV
areas have the potential to cause more
than minimal adverse impacts.
The majority of commenters objected
to the proposed prohibition against the
cultivation of new species by an
operation while recognizing the need to
protect the environment from invasive
species colonization. A few commenters
were in favor of the prohibition citing
concerns about invasive species and
changing culture methods. One
commenter said that this NWP should
not authorize experimental cultivation
of new species in a waterbody.
Upon review of the comments, the
proposed NWP has been modified
slightly. The NWP does not authorize
aquaculture activities for any species
that were not previously cultivated in
the waterbody. However, under this
NWP, an individual operator can change
the species grown under this NWP
within the project area, provided the
change is limited to species that have
been previously cultivated in the water
body. Such a change would require preconstruction notification. The
commercial production of a shellfish
species that has not been previously
commercially produced in the
waterbody, including new exotic (nonnative) species, may only be authorized
by an individual permit or a regional
general permit if applicable. Also, this
NWP does not authorize experimental
cultivation of new species. It only
authorizes on-going commercial
shellfish aquaculture activities,
provided those activities satisfy the
terms and conditions of this NWP.
Experimental cultivation is considered
to be a new activity, and may be
authorized by other DA permits if it
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involves activities subject to the Corps
regulatory jurisdiction.
Producers must be licensed, as
required, through their State’s
regulatory agency. Commercial harvest
will only commence under each State’s
Shellfish Authority, as delegated by the
U.S. Food and Drug Administration
under the National Shellfish Sanitation
Program. To be eligible for coverage
under this NWP, producers must obtain
all required permits or licenses required
for their culture activities, such as
transfer permits, development permits,
and land-use permits.
In response to commenters concerned
about the individual and cumulative
adverse effects to the environment and
the many commenters who stated that
acreage limits were not an adequate way
of establishing or evaluating the
interaction of the shellfish operation
with the aquatic environment, an
additional pre-construction notification
threshold has been added. When an
existing operation decides to change
culture methods, for example to go from
bottom-culture to long-line or from longline to bottom culture, pre-construction
notification is required. These existing
operations may be authorized by this
NWP, after the district engineer has
reviewed the pre-construction
notification and determined that the
new activity complies with the terms
and conditions of the NWP and will
have minimal adverse effects.
We are also committed to conducting
programmatic reviews of commercial
shellfish activities generally to ensure
that the Corps is authorizing only those
activities that result in minimal
individual or cumulative adverse effects
on the aquatic environment with this
NWP or other general permits for
aquaculture activities. These reviews
will begin as soon as possible in all
divisions, and will involve Federal,
State and local agencies, stakeholders,
and the general public to help the Corps
develop future regional and special
conditions to mitigate impacts to the
aquatic environment or other aspects of
the public interest which may result
from commercial shellfish aquaculture
activities. Completion of these
programmatic reviews is not necessary
for authorization under this NWP. The
data collected through the preconstruction notification and reporting
requirements will support these
reviews.
One commenter said that this NWP
should include conditions prohibiting
the use of pesticides. A commenter
stated that this NWP should require preconstruction notification for any activity
located in National Park Service units,
and that review by the National Park
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Service should be conducted before the
activity is authorized by this NWP.
The Corps does not regulate
application of pesticides under Section
10 of the Rivers and Harbors Act of 1899
or Section 404 of the Clean Water Act.
The application of pesticides into
aquatic environments is regulated by
other agencies through other authorities.
We do not agree that pre-construction
notification should be required for ongoing commercial shellfish aquaculture
activities being conducted in areas
under the purview of the National Park
Service. The National Park Service has
the authority to control the activities
conducted in its units, to ensure that
those activities are consistent with any
management requirements or objectives
established for those units.
Proposed NWP D is issued as NWP
48, with the modifications discussed
above.
NWP 49. Coal Remining Activities.
This is a new NWP. It provides for
authorization of projects associated with
the remining and reclamation of lands
that were previously mined for coal.
New mining may be conducted on
adjacent areas provided that the area
mined is smaller than 40 percent of the
previously mined lands plus the
unmined lands required to reclaim the
previously mined lands as determined
by SMCRA. Pre-construction
notification is required for all activities
proposed to be authorized by this
permit, and the permittee must receive
written notification from the District
Engineer prior to commencing the
activity. Additionally, the projects must
be authorized by OSM or by states with
approved programs under Title IV or V
of SMCRA.
One commenter requested that the
proposed NWP be changed to include
Abandoned Mine Land (AML) projects
that are government funded or
contracted. They believed that the
aquatic benefits resulting from the AML
projects are similar in nature to those
that would be covered by this NWP, and
that since this NWP requires
notification, any adverse impacts to
high-quality waters could be avoided.
Another commenter suggested that the
Corps clarify the extent to which NWPs
are required for AML projects, and
another commenter stated that the Corps
should clearly state that no NWP of any
kind is required for projects that fall
under Title IV of SMCRA. One
commenter stated that it is imperative
that the new NWP 49 proposed by the
Corps not inhibit efforts but rather
support recent actions by states, EPA,
and OSM to encourage opportunities for
remining AML impacted lands and
waters.
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We agree that this NWP should
support and encourage opportunities for
remining AML impacted lands and
waters. We are thus modifying the text
of this NWP to authorize AML projects
that include coal extraction authorized
by Title IV of SMCRA, in addition to
remining authorized under Title V. To
authorize Title IV AML projects that do
not involve coal extraction, we have
modified NWP 37, which authorizes
emergency watershed protection and
rehabilitation activities. In response to
the comment that projects conducted
under Title IV of SMCRA should not
require Section 404 authorization, any
discharge of dredged or fill material into
waters of the United States, requires an
authorization under Section 404 of the
Clean Water Act unless the activity is
specifically exempt.
Several commenters agreed that the
Corps should issue an NWP to authorize
remining activities. They stated that
until recently the Corps has not
recognized the environmental benefits
of remining and basically ignored
remining incentives developed by
Congress and other Federal agencies
such as OSM and USEPA. However,
these commenters believe that the
requirement that any newly mined land
not exceed 40 percent of previously
mined land plus any unmined land
necessary for reclamation is
inappropriate. They state that the ratio
should be left up to the SMCRA agency
on a case-by-case basis and that a rigid
40 percent ratio may not allow enough
material to be generated to reclaim the
previously mined land. One commenter
stated that the Corps should reconsider
the proposed limitations since an
overall improvement in aquatic
resources is guaranteed and, as
proposed, the ratio threshold only
serves to limit the reclamation of
abandoned mine lands. One commenter
recommended that the ratio limitation
be removed and that the Corps rely
solely on the demonstration that the
overall project, including the
reclamation activity and any new
mining, will result in a net increase in
aquatic functions. One commenter
stated that the Corps should reconsider
basing permit eligibility on uplands area
(acreage), which is outside the
jurisdiction of the Corps, and instead
focus on the improvement that such
activities would have on the aquatic
resources within the project area, which
is within Corps jurisdiction. Another
commenter said that this NWP should
not authorize coal mining in any new
areas, because of the potential for those
activities to cause more than minimal
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adverse effects on the aquatic
environment.
We would like to clarify that the
‘‘remined’’ area on which the 40 percent
ratio is based includes any unmined
lands required to reclaim the previously
mined lands, as determined by the
SMCRA agency. The allowance for an
additional 40 percent of newly mined
area is above and beyond the area
required to complete the restoration of
the previously mined land. This NWP
was intended to authorize single and
complete projects where a clear majority
of the mining would be considered
remining, and therefore offer operators
incentives to reclaim previously mined
lands. We thus believe that there needs
to be both a limit on new mining and
a requirement for an overall increase in
aquatic resource functions for this NWP.
We believe it is appropriate to authorize
a limited amount of coal mining in new
areas, as long as the remining and
reclamation activities are conducted. In
addition, the adverse effects of any new
mining will be reviewed through the
pre-construction notification process,
and the permittee cannot begin work
until written verification is received
from the district engineer, after
determining that the remining activity,
plus any new mining, will result in
minimal adverse effects on the aquatic
environment.
Proposed Limits
One commenter suggested that while
some impact limits may be appropriate,
the limit should not be based on
drainage area, because such an approach
fails to recognize that small impacts that
occur in the lower reaches of a
watershed may result in more than
minimal adverse effects on the aquatic
environment. One commenter stated
they supported the concept of this NWP
but believe it should have the same
restrictions as NWP 21. Several
commenters recommended that if the
Corps does issue this NWP, it should
include limitations on the linear feet of
stream that can be filled. One
commenter suggested a limit of 1⁄2-acre
per use (which is the same as that
proposed for NWP 50 and other NWPs),
and stated that without such a limit this
NWP would allow impacts that far
exceed those allowed under other
NWPs. One commenter recommended
imposing a 300 linear foot limit for
losses of stream bed. Several
commenters recommended limiting this
NWP to activities that result in the loss
of less than 300 linear feet of streams,
to be consistent with other NWPs.
We did not propose impact limits
based on drainage area. We also do not
believe that specific acreage or linear
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feet of stream limits should be included
on a national basis for this NWP and did
not proposed such limits. If division
engineers believe they need to add
limits at a regional level to ensure that
this NWP authorizes only activities with
minimal adverse effects on the aquatic
environment and which satisfy other
public interest review factors, they may
do so. We believe that at a national level
the ratio limitation and the requirement
for an overall increase in aquatic
function are sufficient to ensure that
this NWP authorize only activities that
produce no more than minimal adverse
impacts, both individually and
cumulatively. Furthermore, this NWP is
used to provide Section 404
authorization for surface coal mining
activities that have also been authorized
by OSM or states with approved
programs under Title IV or Title V of
SMCRA. The Corps believes that the
analyses and environmental protection
standards required by SMCRA in
conjunction with the pre-construction
notification review further ensure that
the NWP activities result in minimal
individual and cumulative adverse
impacts on the aquatic environment. In
fact, this NWP requires a net
environmental benefit in the form of
increased aquatic resource functions,
which will be identified through
functional assessment methods.
Through the pre-construction
notification process, district engineers
can also impose special conditions on a
case-by-case basis to ensure that the
adverse effects on the aquatic
environment are minimal. Also, if the
district engineer determines through
this case-by-case review that the activity
has the potential to result in more than
minimal adverse effects to the aquatic
environment, he or she can exercise
discretionary authority to require an
individual permit.
Functional Analysis
A couple of commenters stated that
the Corps should not require a
functional analysis of the pre-mining
aquatic conditions. They state that in
these cases, water quality is poor and
can only be improved by completion of
the authorized activities. Furthermore,
many of the sites are located on waters
that are listed on a state’s 303(d)
impaired waters lists. A couple of
commenters stated that the Corps’
requirement for a quantified prediction
of the environmental benefits that will
result is unnecessary because EPA data
shows that remining operations will
result in a net increase in aquatic
resource functions. One commenter
stated that, as the Corps has the data to
show that reclamation projects in
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formerly mined areas have a beneficial
environment effect, every permittee
should not need to prove this again, in
a duplication of the SMCRA
requirements. One commenter stated
that the Corps should not specify that a
net overall improvement to the site’s
aquatic functions is required, but should
focus on whether the project will have
minimal impacts to aquatic resources in
the project area.
We agree that remining projects are
generally beneficial, which is one of the
reasons for proposing to issue this new
NWP. However, we must track impacts
and mitigation and show both on an
individual and a cumulative basis that
each project has a minimal impact on
the aquatic environment. This can only
be done by the applicant submitting
information on pre-mining conditions as
well as what they anticipate the post
mining conditions will be. This permit
requires that the reclamation plan result
in a ‘‘net increase in aquatic resource
functions’’. Studies typically show that
remining operations do improve areas
that were degraded by past mining.
However, landscape characteristics
vary, as do mining and reclamation
practices. Furthermore, as an incentive,
this permit also authorizes a limited
amount of new mining in previously
unmined areas adjoining the remined
area. Therefore, improvements to
aquatic resource functions must be
demonstrated for any project authorized
under this NWP. To do this, the
permittee must submit functional
assessments showing that the project as
a whole, including remining,
reclamation and any new mining, will
result in improved functions, such as
water quality, sediment transport or
retention, and habitat, as appropriate for
the specific type of aquatic habitat (e.g.,
stream or wetland). The functional
assessments can be based on
information developed as part of the
SMCRA process, and should clearly
identify and, if possible, quantify, the
functional lift that will be achieved for
each function. We realize the often poor
quality of the environment where these
projects are proposed and appreciate the
benefits to the aquatic environment that
can be achieved by completing these
projects.
We understand coal mining is covered
by many environmental regulations,
however the Corps has determined that
the current SMCRA process does not
adequately address impacts to the
aquatic environment as required under
Section 404 of the Clean Water Act.
Accordingly, this NWP does not
duplicate the SMCRA permit process,
but we rely on that process for
information that is useful in our Section
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404 analyses. We work with the other
agencies to avoid potential duplication
of effort, and currently uses appropriate
work and studies done by or for others
(i.e., ESA or SHPO surveys/findings) in
our analyses of proposed projects.
Mitigation
A couple of commenters stated that
the Corps should not require additional
mitigation beyond what is already
required of the applicant pursuant to the
SMCRA permit, since the permitted
activities will lead to significant water
quality improvements both at the site
and in the watershed. A number of
commenters asserted that the Corps has
not demonstrated that compensatory
mitigation offsets the adverse impacts of
this NWP. Several commenters also
stated that mitigation must be based on
an assessment of stream functions, for
which the Corps has no approved
methods. One commenter recommended
that mitigation should result in at least
a 1:1 replacement of acres lost in order
to achieve no net loss of waters of the
United States from this NWP. Two
commenters stated that the CWA does
not allow the Corps to issue general
permits based on the use of
compensatory mitigation to reduce the
environmental impacts to minimal.
As a result of the pre-construction
notification process the Corps will
review each project proposed for
authorization by this NWP on a case-bycase basis. Additional mitigation may
not be required for a project. However,
this will be determined through the
district engineer’s minimal impact
determination. As stated in our
regulations, we can rely on mitigation in
making a minimal adverse
environmental effects determination
(see 33 CFR 330.1(e)(3)).
The Corps will review the impacts
from the proposed final design using a
functional assessment method. If the
functions gained by the proposed
project exceed the functions lost as a
result of proposed activities then
additional mitigation may not be
required. We are currently developing
new stream functional assessment
protocols for identifying the functions
lost through impacts and the functions
gained or enhanced through mitigation.
General condition 20 establishes the
framework for determining appropriate
mitigation and achieving no net loss of
aquatic resources. The Corps takes into
account the fact that, in certain areas
and circumstances, any compensatory
mitigation required by the Corps may be
fully encompassed or exceeded by
requirements of others (e.g., reclamation
requirements under SMCRA). As long as
the impacts to the aquatic environment
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are fully mitigated, the Corps will not
require additional compensation.
Pre-Construction Notification
Requirement
One commenter requested the preconstruction notification requirement be
removed. One commenter expressed
approval of the requirement that the
applicant receive written authorization
from the district engineer prior to
commencing the activity.
We believe that the pre-construction
notification requirement helps ensure
that no activity authorized by this
permit will result in greater than
minimal adverse impacts, either
individually or cumulatively, on the
aquatic environment, because it requires
a specific case-by-case review of each
project. If the district engineer
determines through this case-by-case
review that the activity has the potential
to result in more than minimal adverse
effects to the aquatic environment, he or
she can exercise discretionary authority
to require an individual permit.
Minimal Adverse Effects
A number of commenters stated that
this NWP would result in more than
minimal adverse environmental effects,
particularly on a cumulative basis, and
would result in significant degradation
of streams. Therefore, the commenters
believe NWPs should not be used to
authorize these activities, and these
activities should require individual
permits. Several commenters cited the
2002 programmatic Environmental
Impact Statement on surface coal
mining, which documented impacts to
waters, particularly in Appalachia. A
few commenters cited studies
conducted by EPA and other research
on the ecological impacts of valley fill
on streams and on fish populations.
We believe that a careful case-specific
minimal impact determination is
necessary for this NWP. In addition, as
with NWP 21, this NWP requires a
written verification before the project
proponent may proceed with the work.
The applicant must clearly demonstrate
that the reclamation plan will result in
a net increase in aquatic resource
functions, and that any adverse impacts
to the aquatic environment are minimal.
If the district engineer determines
through this case-by-case review that
the activity has the potential to result in
more than minimal adverse effects to
the aquatic environment, he or she can
exercise discretionary authority to
require an individual permit.
Since the functions of aquatic
resources vary widely across the
country, assessment of cumulative
impacts is conducted by Corps districts
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on a watershed basis, based on regional
and local conditions and procedures. If
the use of this NWP results in more than
minimal cumulative adverse effects on
the aquatic environment in a watershed,
the division engineer may modify,
suspend, or revoke this NWP in that
watershed. We believe the preconstruction notification requirements
for this NWP ensures that authorized
activities result in no more than
minimal adverse impacts to the aquatic
environment because each project is
reviewed on a case-by-case basis and the
district engineer either makes a minimal
impacts determination on the project or
asserts discretionary authority and
requires an individual permit.
Additionally, as noted above, division
engineers can add regional conditions to
any NWP to further restrict the use of
the NWP to ensure that the NWP
authorizes only activities with no more
than minimal adverse effects on the
aquatic environment in a particular
watershed or other geographic region.
Each district tracks losses of waters of
the United States authorized by
Department of the Army permits,
including verified NWPs, as well as
compensatory mitigation achieved
through aquatic resource restoration,
creation, and enhancement.
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Impoundments
Several commenters stated that coal
slurry impoundments should not be
authorized by this NWP. The
commenters also stated that NWPs 21,
49 and 50 cannot be used for both valley
fills and coal slurry impoundments, as
they are not activities that are ‘‘similar
in nature’’, as required for authorization
under an NWP.
The NWPs are issued in accordance
with Section 404(e) of the CWA. NWPs
authorize categories of activities that are
similar in nature. The ‘‘similar in
nature’’ requirement does not mean that
activities authorized by an NWP must
be identical to each other. We believe
the ‘‘categories of activities that are
similar in nature’’ requirement of
Section 404(e) is to be interpreted
broadly, for practical implementation of
the NWP program. NWPs as well as
other general permits are intended to
reduce administrative burdens on the
Corps and the regulated public. We
believe that slurry impoundments are
support features associated with coal
mining and thus can be authorized by
this NWP. However, the impacts
associated with any such
impoundments must be addressed in
the required demonstration that the
project will result in a net increase in
aquatic resource functions.
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Scope of Analysis
One commenter stated that only poor
and isolated communities are being
affected by surface coal mining. Another
commenter noted that coal slurry
impoundments can fail and release
mining wastes into downstream waters.
Two commenters stated that loss of
forest and movement of dirt associated
with surface coal mining has
detrimental environmental effects.
Impacts to poor and isolated
communities are outside of the Corps’
scope of analysis pursuant to the
National Environmental Policy Act. The
Corps evaluation of coal mining
activities is focused on impacts to
aquatic resources. In accordance with
E.O. 12898, the Corps has determined
that the issuance of the NWPs,
including NWP 49, will not cause
disproportionate impacts to minority or
low-income communities (see
discussion of E.O. 12898 below). The
design and safety of coal slurry
impoundments are more appropriately
addressed through the SMCRA process,
which provides design and safety
requirements for these facilities. Mining
in general is permitted under a separate
Federal law, the Surface Mining Control
and Reclamation Act. Impacts
associated with surface coal mining and
reclamation operations are
appropriately addressed by the Office of
Surface Mining or the applicable state
agency. Where relevant to potential
impacts on aquatic resources, the Corps
considers documentation prepared
pursuant to SMCRA in its review of preconstruction notifications.
Public Participation
Several commenters stated that this
NWP does not provide the public with
an opportunity to comment on the
specific conditions of the NWP
authorizations that affect their
communities and watersheds.
Section 404(e) of the Clean Water Act
provides the statutory authority for the
issuance of general permits on a
nationwide basis for any category of
activities that the Corps determines will
have minimal adverse impacts on the
aquatic environment, both individually
and cumulatively. The Corps establishes
NWPs in accordance with section
404(e), by publishing and requesting
comments on the proposed permits. The
general public has the opportunity to
comment on NWPs at this time. In order
to address the requirements of the
National Environmental Policy Act, the
Corps prepares an environmental
assessment for each NWP, as well as a
404(b)(1) Guidelines analysis if the
NWP authorizes activities under Section
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404 of the Clean Water Act. The
decision document discusses the
anticipated impacts on the Corps’ public
interest factors from a national
perspective. NWPs are issued at the
conclusion of this process. The
individual projects that are proposed for
authorization under an NWP are not
given a permit but a verification or
authorization that the project complies
with an NWP. There are no
requirements for public comments on
specific projects authorized under
NWPs. However, as noted above, one of
the bases for our determination that the
activities authorized by this NWP will
have minimal impacts is that they must
also be authorized by a permit issued
under SMCRA, which requires many of
the same types of analyses that we
would require under Section 404. In
addition, each SMCRA permit action
includes a public participation process.
Therefore, as a practical matter, the
public will have the opportunity to
comment on each individual project
authorized under this NWP.
General
One commenter stated that there is no
rational basis for the creation of this
proposed NWP since under SMCRA, the
term ‘‘surface coal mining operations’’
includes both Title V permits
authorizing remining of previouslymined lands as well as mining of lands
that have not been previously disturbed.
The commenter stated that the NWP
may not conform to the Section
404(b)(1) Guidelines, which would
require greater scrutiny for remining
activities due to the availability of
existing benches, roads and fills that
could render new fill in waters of the
United States unnecessary. The
commenter also cited Section 301(p) of
the Clean Water Act, which allows
exceptions to effluent limits for surface
coal remining operations. The
commenter asserted that Section 404
does not have a similar exception for
remining, and that this NWP cannot
replace the requirements for avoidance,
minimization and mitigation with the
proposed amorphous standard of a ‘‘net
increase in aquatic resource function’’.
The commenter also stated that it was
unclear from the text of this NWP how
the Corps intends the remining
authorization to work.
New coal mining activities eligible for
authorization under this NWP may be
authorized by NWP 21, but in contrast
to NWP 21 this NWP also authorizes
abandoned mined land reclamation
activities under Title IV of SMRCA that
involve coal extraction. We recognize
the benefits of restoration of mine sites
that are causing physical and or
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chemical impacts to waters of the
United States and the fact that due to
changes in technology, additional coal
may be excavated as part of the
reclamation process. These sites may
also be combined with adjacent
unmined areas to develop a project that
is economically viable. The net result of
these combined remining/new mining
projects is that sources of pollution to
downstream waters, including acid
mine drainage and sediment, will be
eliminated or substantially reduced
when the site is reclaimed. We believe
this NWP will encourage applicants to
consider reclamation of adjacent lands
in their overall project plans. As noted
previously, the applicant needs to show
through a functional assessment method
that the project will result in a net
increase in aquatic resource functions.
As noted previously, Section 404(e) of
the Clean Water Act provides the
statutory authority for the issuance of
general permits on a nationwide basis
for any category of activities. As part of
the establishment of the NWPs a
decision document is prepared for each
NWP along with a 404(b)(1) Guidelines
analysis. Although analysis of offsite
alternatives is not required in
conjunction with general permits, each
proposed project is evaluated for onsite
avoidance and minimization, in
accordance with general condition 20,
Mitigation. This includes consideration
of the availability of existing benches,
roads, and fills that could be used
instead of placing new fill in waters of
the United States.
Proposed NWP E is issued as NWP 49,
with the addition of authorization for
projects authorized under Title IV of
SMCRA that include coal extraction.
NWP 50. Underground Coal Mining
Activities. This is a new NWP. Preconstruction notification is required for
all activities proposed to be authorized
by this permit. As with NWP 21,
permittees must receive written
authorization from the Corps before
proceeding. Additionally, the projects
must be authorized by OSM or by states
with approved programs under Title V
of SMCRA.
applied to small streams could result in
the fill of long segments of streams
without proper mitigation. Two
commenters stated that if NWP 50 is
issued, it must include stringent limits
on the amount of stream that can be
filled. One commenter stated that the
NWP should be limited to activities that
fill less than 300 feet of streams and
should not be used in watershed where
the cumulative amount of filled streams
is already likely causing more than
minimal harm.
In consideration of the comments
received, we have decided not to
include the 1⁄2-acre limit. This permit
replaces the 2002 version of NWP 21 for
underground coal mining activities. The
new NWP 21, which continues
authorization for surface coal mining
activities, does not include an acreage
limit. Instead, NWP 21 relies on the
SMCRA permitting process in
combination with an enhanced preconstruction notification requirement
which requires that permittees wait for
written verification from the Corps
before beginning their projects, even if
the pre-construction notification review
takes more than 45 days. After further
consideration, we have determined that
the same logic that applies to NWP 21
also applies to NWP 50, and so have
adopted similar requirements with
respect to limits and verification. Thus,
the 1⁄2 acre limit has been dropped, and
permittees must wait for written
verification from the Corps before
proceeding.
Proposed Limits
Numerous comments were received
regarding the proposed 1⁄2 acre limit on
this NWP. Many commenters stated that
the 1⁄2 acre limit is too small to
accommodate underground coal mining
activities and attendant features and it
should be deleted. One commenter
recommended that any limits should be
imposed regionally rather than
nationally.
One commenter stated that the 1⁄2 acre
limit was too high and the 1⁄2 acre limit
Use of NWP 21 for Underground Mining
Concerns were expressed by several
commenters regarding the continued
use of NWP 21 to authorize
underground mining activities. These
commenters requested clarification
regarding this issue. One commenter
noted that if NWP 21 could not be used
for underground mining then most
underground mine discharges would
require an individual permit. One
commenter expressed concerns
regarding the use of NWP 21 for coal
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Pre-Construction Notification
Four commenters recommended that
applicants should be required to receive
written authorization prior to
commencing the activity. As noted
above, the Corps has now adopted this
requirement for this permit and dropped
the 1⁄2 acre threshold. This requirement
is necessary to give the district engineer
adequate time to determine whether or
not to assert discretionary authority and
require an individual permit if the
impacts of the proposed activity are
more than minimal, either individually
or cumulatively.
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preparation and processing activities
outside of the mine site. The commenter
noted that preparation activities were
not part of a surface coal mining project.
The Corps envisions that activities
that are not part of the underground
mine site, which are outside the SMCRA
permit area, can be authorized by NWP
21 if they met the conditions for its use.
We note that many processing plants
serve both underground and surface
mine sites, some at considerable
distance, and that construction of such
plants does not involve underground
disturbances in the way that
underground mining does. Thus we
believe it appropriate to continue
allowing NWP 21 to authorize such
activities. We believe the changes
discussed above to NWP 50 address the
concern that, under the proposed
version of the permit, many
underground coal mining activities
would have required an individual
permit. There is no longer an acreage
limit on the use of this permit, although
it can only be used to authorize
activities which the district engineer has
determined will have no more than
minimal adverse effects, both
individually and cumulatively, and only
after the district engineer has notified
the operator in writing that use of this
NWP is authorized.
Minimal Adverse Impacts
Many commenters were opposed to
issuance of this NWP. They stated that
general permit procedures were
inappropriate for such large scale
activities and that these types of
activities seemed to demand a thorough
review, public notice, and an
alternatives and minimization analysis.
One commenter stated that the Clean
Water Act does not allow the Corps to
issue general permits on the basis that
compensatory mitigation will reduce net
adverse effects to a minimal level. Two
comments stated that NWPs can only be
used for activities that cause minimal
environmental effects both individually
and cumulatively, and if impacts are
more than minimal, the project requires
an individual permit with site-specific
analysis and public comment. Several
commenters stated that coal mining
results in significant environmental
impacts and degradation of streams in
Appalachia.
The Corps believes that a careful casespecific determination of impacts is
necessary for this NWP. The preconstruction notification process, along
with the requirement for written
verification from the Corps, will allow
the district engineer to determine if the
impacts of the proposed activity are no
more than minimal, individually and
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cumulatively, or whether an individual
permit is required. Furthermore, we
believe that the Corps can rely on
mitigation in making a minimal adverse
environmental effects determination.
We believe that an assessment of
individual and cumulative impacts
cannot be made on a national level,
because the functions and values of
aquatic resources vary widely across the
country. Assessment of cumulative
impacts is more appropriately
conducted by Corps districts on a
watershed basis, based on regional and
local conditions and procedures. We
believe our process for this NWP
ensures that activities authorized by the
NWP result in no more than minimal
adverse impacts to the aquatic
environment because each project is
reviewed on a case-by-case basis and the
district engineer either makes a minimal
impacts determination on the project or
asserts discretionary authority and
requires an individual permit.
Additionally, as noted above, division
engineers can add regional conditions to
any NWP to further restrict the use of
the NWP to ensure that the NWP
authorizes only activities with no more
than minimal adverse effects on the
aquatic environment in a particular
watershed or other geographic region.
Each district tracks losses of waters of
the United States authorized by
Department of the Army permits,
including verified NWPs, as well as
compensatory mitigation achieved
through aquatic resource restoration,
creation, and enhancement.
Furthermore, as with NWP 21, all
activities authorized by this permit
require authorization under SMCRA,
and the SMCRA analysis,
documentation and process
requirements largely substitute for the
analysis, documentation and process
requirements of an individual permit.
This is not to say that discharges related
to coal mining and their impacts on
aquatic resources do not require
independent review and authorization
by the Corps with respect to the
requirements of the CWA, but the Corps
believes that the analytical and process
requirements can be streamlined by
relying on the SMCRA process to the
extent appropriate. Where the district
engineer determines that these process
requirements are not adequate for a
particular project, he or she will require
an individual permit.
404(b)(1) Guidelines
Several commenters stated that any
proposed disturbance to waters to
support coal processing or underground
coal mining activities should be subject
to the Section 404(b)(1) Guidelines, and
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that alternatives that do not result in
impacts to waters of the United States
are available.
As noted previously, Section 404(e) of
the Clean Water Act provides the
statutory authority for the issuance of
general permits on a nationwide basis
for any category of activities. As part of
the establishment of the NWPs a
decision document is prepared for each
NWP along with a 404(b)(1) Guidelines
analysis. Although analysis of offsite
alternatives is not required in
conjunction with general permits, each
proposed project is evaluated for onsite
avoidance and minimization, in
accordance with GC 20. This includes
consideration of alternatives that do not
result in impacts to waters of the United
States.
One commenter stated that it was a
duplication of effort to have a review of
the applicants’ reclamation plan.
The Corps understands coal mining is
covered by many environmental
regulations, however the Corps has
determined that SMCRA does not
currently adequately address impacts to
the aquatic environment as required
under Section 404 of the CWA.
Therefore this NWP does not duplicate
the SMCRA permit process but does rely
on it for information used in the
analysis. The Corps continues to work
with the other agencies to avoid
potential duplication of efforts. The
reclamation plan can be used to
consider proposed mitigation measures
for the projects being proposed for
authorization by NWP 50. This
information will be used by the Corps
in making a determination as to whether
the impacts are no more than minimal.
Scope of Analysis
One commenter stated that there
should be a way to figure out how to
extract the coal and still protect the
environment. Another commenter noted
that the amount of earth moving by
mining activities is sufficient by itself to
demonstrate that environmental impacts
of mining are significant. One
commenter stated that the subsidence
that may occur as a result of
underground mining should be
considered in determining the acreage
impacts to waters for this NWP. One
commenter noted that coal mining
waste contains chemical components
that are toxic to aquatic life and that
waste impoundments may fail. The
commenter believed that this justifies an
independent review. One commenter
stated that the ‘‘facing up’’ practice
cannot be carved out from the full range
of environmental impacts associated
with underground mining operations
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and must be reviewed comprehensively
and not piecemeal.
The Corps evaluation of coal mining
activities is focused on impacts to
aquatic resources. Other impacts of coal
mining are addressed under a separate
Federal law, SMCRA. Such impacts,
including those associated with
reclamation operations, are
appropriately addressed by OSM or the
applicable state agency, if program
delegation has occurred. To the extent
that reclamation activities affect waters
of the United States, these will be
addressed in the Corps review and
appropriate mitigation required.
Similar in Nature
Several commenters stated that slurry
impoundments should not be allowed
under NWPs, and that NWPs can only
be issued for activities that are similar
in nature. The Corps has determined
that slurry impoundments are related to
underground mining activities. The
NWPs are issued in accordance with
Section 404(e) of the CWA. NWPs
authorize categories of activities that are
similar in nature. The ‘‘similar in
nature’’ requirement does not mean that
activities authorized by an NWP must
be identical to each other. We believe
the ‘‘categories of activities that are
similar in nature’’ requirement of
Section 404(e) is to be interpreted
broadly, for practical implementation of
the NWP program.
Mitigation
Several commenters stated that the
mitigation done for coal mining impacts
is scientifically indefensible and, absent
such mitigation, the projects authorized
under NWP 50 have more than minimal
adverse effect and are therefore not
eligible for an NWP. They stated that
current mitigation projects have so far
been unsuccessful and referenced a
court case in the Southern District of
West Virginia (Ohio Valley
Environmental Coalition v. Bulen),
where they noted that a Corps official
stated that he did not know of a single
instance of successful headwater stream
creation. Also, the commenters stated
that the Corps did not include any
specific guidelines for how to assess
stream function in order to determine
the adequacy of compensatory
mitigation. They also stated that the
Corps has not shown that mitigation
will offset the impacts authorized under
NWP 50 or that off-site enhancement of
streams would fully compensate for
functions of streams that are destroyed.
Other commenters stated that the Corps
mistakenly allows the mitigation
requirements of SMCRA and state water
quality laws to satisfy the independent
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requirements of Section 404 of the Clean
Water Act. They stated that allowing a
permittee to claim a compensatory
mitigation or reclamation activity
already required under SMCRA as
compensatory mitigation under the
Clean Water Act is ‘‘double-counting’’
and improperly blurs the requirements
of sequencing (i.e., avoidance,
minimization, mitigation) imposed
under the 404(b)(1) guidelines. Other
commenters recommended that a
mitigation ratio of at least 1:1 should be
required in order to achieve no net loss,
and that mitigation also should be
required for potential, as well as actual,
impacts. Several commenters stated that
final reclamation of wetland habitat will
most likely occur in the absence of
required compensatory mitigation.
In order to ensure that an activity
results in no more than minimal adverse
effects on the aquatic environment, the
Corps will add permit conditions that
require compensatory mitigation that
meets specified success criteria. The
Corps will generally require the
permittee to monitor the mitigation site
for five years and, if the mitigation site
does not meet the success criteria at that
time, remediation or additional
mitigation will be required. This
ensures that the authorized activity will
not result in a net loss in aquatic
functions. The Corps has increased its
compliance efforts to ensure that
projects authorized by DA permits are
constructed as authorized and that
mitigation is successful.
We are currently developing new
stream functional assessment protocols
to identify and quantify the functions
lost through authorized impacts and the
functions gained or enhanced through
mitigation. The Corps coordinates with
the SMCRA and state resource agencies
to achieve appropriate aquatic
restoration on mine sites, which can
reduce or eliminate the amount of offsite compensatory mitigation needed.
The Corps does not consider this
‘‘double-counting’’, because the areas
restored are only counted once in the
replacement of aquatic resource
functions. As long as the functions lost
as a result of the permitted activity are
mitigated through the onsite restoration
or enhancement, it does not matter if the
restoration also meets other goals
unrelated to the Section 404 impacts.
General condition 20 establishes the
framework for achieving no net loss of
waters/wetlands, as well as the
sequential review of mitigation
approaches on-site. The Corps takes into
account the fact that, in certain areas
and circumstances, any Corps
compensatory mitigation requirement
may be fully encompassed or exceeded
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by requirements of others. As long as
the impacts to the aquatic environment
are fully mitigated, the Corps will not
require additional compensation.
Proposed NWP F is issued as NWP 50,
with the modifications discussed above.
General Conditions
One commenter supported the
proposed change to the ordering of the
general conditions. One commenter said
that the proposed changes to general
conditions will reduce environmental
protection. A commenter stated that
temporary impacts should be addressed
through a new general condition,
instead of requiring separate
authorization under NWP 33.
The changes to the general conditions
will help improve environmental
protection, by providing clearer and
more enforceable requirements for
permittees. Department of the Army
permits are required for temporary
structures, work, or discharges into
waters of the United States, including
navigable waters, unless those activities
are exempt from permit requirements.
Therefore, those regulated activities
cannot be authorized through a general
condition. In some cases, temporary
structures, work, or discharges
associated with another permitted
activity are included in the NWP
authorization for that activity; in other
cases temporary structures, work or
discharges must be authorized
separately under NWP 33.
One commenter said that the
proposed ‘‘Note’’ for the NWP general
conditions should contain language
requiring permittees to comply with
regional conditions and state water
quality standards. This commenter also
requested that the word ‘‘should’’ be
replaced with ‘‘must.’’
The proposed ‘‘Note’’ clearly states
that permittees are required to comply
with regional conditions and that
permittees should check on the status of
water quality certifications and Coastal
Zone Management Act consistency
determinations before using an NWP.
We cannot require prospective
permittees to contact district offices to
obtain this information (hence we have
not replaced ‘‘should’’ with ‘‘must’’) but
we have clarified that individual
certification is required in cases where
prior certification for the NWP has not
been received. Permittees may also be
able to obtain information on regional
conditions and the status of water
quality certifications and Coastal Zone
Management Act consistency
determinations through the Internet or
other sources.
One commenter recommended adding
a new general condition to address the
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downstream movement of substrate and
wood. This general condition would
require stream crossings, such as bridges
and culverts, to allow downstream
movement of substrate and wood during
100-year flow events, as well as
movement of wood from upstream
segments to downstream segments.
Another commenter suggested adding a
new general condition to address
adverse impacts from invasive species.
We do not agree that it is necessary
to add a new general condition, as there
are other general conditions which
already include adequate provisions to
address this concern. General condition
2, Aquatic Life Movements, states that
no activity may substantially disrupt the
necessary life-cycle movements of those
species that normally migrate through
the area. General condition 9,
Management of Water Flows, states that,
to the maximum extent practicable, the
activity must not restrict or impede the
passage of normal or high flows, unless
the primary purpose is to impound
water. In general, blockages caused by
restricted movement of wood or
substrate would violate these conditions
and must be prevented. Further, the
ability for division and district
engineers to exercise discretionary
authority or regionally condition
proposed activities under an NWP are
sufficiently to address any site-specific
concerns related to blocked movement
of wood and ensure that authorized
activities result in minimal adverse
effects on the aquatic environment. The
Corps does not have the regulatory
authority to prohibit the introduction of
invasive species. Invasive species may
become established in areas through
many mechanisms, not just disturbances
caused by construction activities
authorized by NWPs and other Corps
permits. Such a condition would also be
unenforceable and therefore such a
general condition would be contrary to
33 CFR 325.4(a).
A number of commenters objected to
the removal of the phrase ‘‘including
structures or work in navigable waters
of the United States or discharges of
dredged or fill material’’ from text of
certain general conditions. One
commenter asked if removal of that
phrase from those general conditions
would reduce protection of aquatic
resources.
The removal of that language will not
affect protection of waters of the United
States. The stricken language was
considered redundant as it simply refers
to the general types of activities
regulated under sections 10 and 404.
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General Conditions
GC 1. Navigation. We proposed to
modify this general condition to require
permittees to install any safety lights
and signals prescribed by the U.S. Coast
Guard. We also proposed to modify this
general condition to notify permittees
that they may be required to remove
structures or work that cause
unreasonable obstruction to navigation.
One commenter supported the
requirement concerning safety lights
and signals. One commenter said that
the Federal government should bear the
financial costs for the removal of
structures or work it authorized. One
commenter stated that the Federal
government itself could be a permittee
and be required to remove the structure
or work at the Federal government’s
expense. One commenter said that this
general condition should also include
waters determined by states to be
navigable waters.
There may be cases where activities
authorized by Department of the Army
permits interfere with navigation or an
existing or future operation of the
United States and need to be removed.
The cost of removal is the responsibility
of the permittee, even in cases where
the permittee is the Federal government.
If there is any question as to whether or
not a particular activity or structure will
interfere with navigation, the permittee
should check with the Coast Guard
before beginning the activity. Adverse
effects to navigable waters identified by
states that are not navigable waters of
the United States should be addressed
by state regulatory programs. The Corps
lacks the authority to enforce state laws
and regulations for state navigable
waters.
The general condition is adopted as
proposed.
GC 2. Aquatic Life Movements. We
proposed to modify this general
condition by adding the phrase ‘‘if
known’’ before ‘‘necessary life cycle
movements’’ because those life cycle
movements that are important are not
always well understood for indigenous
aquatic species. The intent of this
general condition is to ensure that the
necessary movements of aquatic species
are not substantially disrupted.
Many commenters expressed
opposition to the proposed modification
and recommended removing the phrase
‘‘if known.’’ They stated that the lack of
knowledge concerning aquatic life
movements should not be construed as
authorization to allow disruption of
aquatic life cycle movements. One
commenter supported the proposed
modification, and also recommended
adding ‘‘at the time of the permit
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application, if known, or if documented
at the time of application.’’ to this
general condition.
Activities authorized by NWPs should
not substantially disrupt the necessary
life cycle movement of aquatic species,
and the absence of species-specific
information does not mean measures
cannot be taken to prevent unnecessary
obstructions to those movements. Even
if the necessary life cycle movements
are not known, inferences can be made
to help ensure that those movements
can continue. Those inferences can be
based on general considerations of the
mitigation measures necessary to ensure
that adverse impacts to aquatic life
movements are minimized to the
maximum extent practicable. For
example, properly sized culverts that
are installed to retain low flow
conditions will help ensure that life
cycle movements will continue.
Therefore, we are removing the phrase
‘‘if known’’ from this general condition
to allow district engineers to continue to
use their judgment, so that adverse
effects to aquatic life movements are
minimized, even if the necessary life
cycle movements are not known, but
can be generally inferred.
Two commenters requested
clarification of the term ‘‘substantially’’
as used in this general condition. One
commenter said that this term results in
too high a threshold for the disruption
of aquatic life movement. One
commenter stated that aquatic life
movement should be reviewed using
hydraulic analyses performed for the
range of flows expected after a basin is
fully developed. Another commenter
said that this general condition should
require stream crossings to be
constructed with bottom elevations
below the normal substrate grade to
avoid creating improper elevations or
barriers that may substantially disrupt
aquatic life movements. This
commenter also recommended
modifying this general condition to
prohibit changes to stream morphology
that could substantially interfere with
aquatic life movements.
In general, activities in waters of the
United States authorized by NWPs are
likely to result in some disruption of
necessary life cycle movements of
aquatic species, since we are
authorizing discharges of dredged or fill
material into those waters or structures
or work in navigable waters of the
United States. The word ‘‘substantially’’
supports the requirement that NWPs
authorize only those activities that
result in minimal individual and
cumulative adverse effects on the
aquatic environment, while recognizing
that some disruption may occur. Some
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disruptions to aquatic life movement are
measurable but not substantial, and may
be acceptable during construction or
during natural seasonal events such as
floods, winter ice conditions, or during
construction conducted during dry
seasons. It is not practicable,
appropriate, or necessary to conduct
hydrologic analyses for each NWP
activity that has the potential to disrupt
life cycle movements, based on the
projected development for a watershed.
Compliance with this general condition
is to be assessed on a case-by-case basis,
through available information or general
knowledge of aquatic life movements.
The current language in the general
condition, especially the requirement to
install culverts to maintain low flow
conditions, is sufficient to ensure that
stream crossings do not substantially
disrupt aquatic life movements. This
general condition, as well as the
requirements of general condition 9,
Management of Water Flows, will help
ensure that NWP activities result only in
minimal adverse effects to the
movement of aquatic life via streams.
The general condition is adopted,
with the modification discussed above
GC 3. Spawning Areas. We proposed
to modify this general condition by
removing language describing the
general types of activities authorized by
NWPs under sections 10 and 404.
One commenter stated that not
enough protection is provided since
avoidance is only necessary to the
maximum extent practicable. One
commenter requested a definition of the
term ‘‘important spawning area.’’ One
commenter said that this general
condition should not apply to NWPs 27
or 48 because shellfish seeding can
provide and/or increase availability of
spawning habitat.
The removal of language describing
the general applicability of NWPs will
not affect protection of waters of the
United States. This general condition
applies to all NWPs. The phrase ‘‘to the
maximum extent practicable’’ is
necessary since some NWP activities
may be time-sensitive and it is not
possible to completely avoid activities
in spawning areas. Since the NWPs
authorize activities that have minimal
adverse effects on the aquatic
environment, some NWP activities may
be conducted in spawning areas.
Identification of important spawning
areas is more appropriately addressed
through either the regional conditioning
processes or through the assessment of
site-specific characteristics during the
review of pre-construction notifications.
The general condition is adopted as
proposed.
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GC 4. Migratory Bird Breeding Areas.
We proposed to modify this general
condition to cover migratory birds
generally, not just migratory waterfowl.
We also proposed to remove language
describing the general types of activities
authorized by NWPs under sections 10
and 404.
One commenter said that the
proposed modification would further
restrict the use of the NWPs in
wetlands. Another commenter asked
how the change would affect nonwaterfowl migratory birds in cases
where their habitat requirements are
different than the habitat requirements
of waterfowl. One commenter fully
supported the inclusion of migratory
birds but requested a national no-work
timing window in breeding areas from
March 1 to July 15 to reduce uncertainty
associated with the phrase ‘‘to the
maximum extent practicable.’’ Another
commenter indicated that this general
condition should prohibit haying or
grazing during the nesting season unless
an emergency is declared. One
commenter said that the proposed
changes do not comply with the
Migratory Bird Treaty Act and suggested
that breeding areas should ‘‘be avoided
to the maximum extent practicable to
assure minimal adverse impact on
migratory birds and their breeding
areas.’’ This commenter asserted that
authorized activities under any NWP
must comply with the Migratory Bird
Treaty Act. This commenter also urged
expansion of the general condition to
include protection of Important Bird
Areas, which is an initiative by nongovernmental entities to protect avian
species of conservation concern.
Another commenter said that this
general condition should also state that
the take of migratory birds, their eggs,
nests, or parts is not allowed under the
Migratory Bird Treaty Act without a
permit.
Aquatic resources provide a diverse
variety of breeding habitats for a wide
variety of migratory avian species. The
replacement of ‘‘waterfowl’’ with
‘‘migratory birds’’ will help reduce
adverse impacts to aquatic habitats that
are breeding areas of all migratory birds,
not just waterfowl. It is not practicable
to identify a uniform window of 41⁄2
months during which no activities in
any habitat potentially used as breeding
areas by migratory birds is allowed.
Furthermore, breeding patterns and
seasons vary by region. Time-of-year
restrictions to protect breeding areas are
thus more appropriately addressed
through regional conditions imposed by
division engineers or special conditions
added to NWP authorizations by district
engineers. It would not be appropriate
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to amend this general condition to
prohibit haying or grazing during
nesting seasons for migratory birds,
since the Corps cannot enforce such a
provision.
The applicability of the Migratory
Bird Treaty Act is addressed by
Executive Order 13186,
‘‘Responsibilities of Federal Agencies to
Protect Migratory Birds,’’ which was
issued on January 10, 2001. This
Executive Order does not apply to
Department of the Army permits.
Responsibility for complying with
requirements of the Migratory Bird
Treaty Act lies with the permittee, but
this responsibility is independent of the
Department of the Army permit. The
provisions of the Migratory Bird Treaty
Act are implemented by the U.S. Fish
and Wildlife Service through the
issuance of take permits under
appropriate circumstances. It would not
be appropriate to modify this general
condition to include an explicit
reference to Important Bird Areas,
though to the extent that they are
encompassed by the phrase,
‘‘waters...that serve as breeding areas for
migratory birds,’’ they are already
covered. There is no Federal statute or
authority for establishing these areas.
We believe the general condition as
written is adequate to protect migratory
birds.
The general condition is adopted as
proposed.
GC 5. Shellfish Beds. We proposed to
remove language describing the general
types of activities authorized by NWPs
under sections 10 and 404. We also
proposed to add proposed NWP D,
Commercial Shellfish Aquaculture
Activities to the exception in this
general condition.
One commenter stated that ‘‘areas of
concentrated shellfish populations’’
should be defined. One commenter said
that the general condition is too
restrictive and should instead provide
the district engineer with discretion to
prohibit an activity that may have a
deleterious effect on shellfish.
It would be inappropriate to define
the term ‘‘areas of concentrated shellfish
populations’’ at the national level. Such
determinations should be made on a
case-by-case basis, and take into account
the characteristics of the shellfish
species inhabiting the waters in which
the NWP activity is located. Criteria for
identifying areas of concentrated
shellfish populations may vary by
species and region. With the exception
of NWPs 4 and 48, the NWPs should not
authorize activities in concentrated
shellfish beds to ensure that the
activities authorized by NWPs result in
minimal adverse effects on the aquatic
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environment. However, the district
engineer may determine that this
general condition does not apply in
situations where a specific NWP activity
will have little or no adverse effect on
areas of concentrated shellfish
populations. The reference to NWP D
has been changed to NWP 48, to reflect
the number assigned to that new NWP.
This general condition is adopted
with the modification discussed above.
GC 6. Suitable Material. We proposed
to modify this general condition by
removing language describing the
general types of activities authorized by
NWPs under sections 10 and 404.
One commenter suggested the general
condition contain a list of suitable
materials rather than a list of unsuitable
materials. One commenter said that
asphalt should be removed from the list
of examples in the general condition
because research has shown that cured
asphaltic concrete is inert. One
commenter asserted that the general
condition does not go far enough to
protect aquatic resources, and
recommended changing the text to
prohibit ‘‘unacceptable chemical
pollution’’ instead of requiring material
to be free of toxic pollutants in toxic
amounts. This commenter also said that
the use of substances such as creosote
and pentachlorophenol in open waters
should be prohibited. One commenter
suggested that the general condition
contain language that the fill material
must be obtained from an upland source
and require it to be sufficiently sized
and shaped to resist erosion for normal
and expected high flows.
We do not agree that it is necessary
to further define what constitutes
‘‘suitable material’’ for the purposes of
this general condition. It is impractical
to provide a comprehensive list of
unsuitable materials. If there are
questions concerning the suitability of a
particular material, the permittee should
contact the appropriate Corps district
office and ask if that material is
considered suitable for the purposes of
this general condition. We continue to
believe that ‘‘asphalt’’ is an unsuitable
material for use in waters of the United
States. Use of substances such as
creosote and pentachlorophenol is
prohibited by general condition 6,
Suitable Material, if they would be
released into the environment in toxic
amounts. It is inappropriate to limit fill
material only to material obtained from
uplands, since material excavated from
aquatic environments may also be
suitable. Other general conditions, such
as general conditions 12 (Soil Erosion
and Sediment Controls) and 9
(Management of Water Flows) address
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requirements for withstanding water
flows.
This general condition is adopted as
proposed.
GC 7. Water Supply Intakes. We
proposed to modify this general
condition by removing language
describing the general types of activities
authorized by NWPs under sections 10
and 404. We also proposed to add the
phrase ‘‘or improvement’’ to account for
adjustments of the public water supply
intake structure that may be necessary
to maintain or improve levels of service.
One commenter supported the
proposed change. One commenter stated
the general condition is overly
restrictive and that the standard should
be that activities that are likely to cause
an impact to a public water supply
intake should be prohibited. One
commenter requested we define
‘‘proximity.’’
This general condition is not too
restrictive, given the importance of
water supply intakes for public,
commercial and industrial use. District
engineers will determine on a case-bycase basis what is necessary to comply
with this general condition. We believe
the term ‘‘proximity’’ is flexible enough
to allow district engineers to determine
that activities that will not adversely
impact a public water supply intake are
not in proximity to the intake. The term
‘‘proximity’’ should be defined on a
case-by-case basis, after taking into
account site characteristics and the
nature of the waterbody and activity.
This general condition is adopted as
proposed.
GC 8. Adverse Effects from
Impoundments. We proposed to modify
this general condition by removing
language describing the general types of
activities authorized by NWPs under
sections 10 and 404.
One commenter recommended
amending the language to prohibit the
use of the NWPs in waters accessible to
anadromous salmonids.
While the Corps recognizes the
importance of protecting aquatic
species, including salmonids, it would
not be practicable to prohibit use of
NWPs in all waters accessible to
anadromous salmonids. Restricting or
prohibiting the use of NWPs in waters
inhabited by anadromous salmon
species is more appropriately addressed
through regional conditions imposed by
division engineers, or assertion of
discretionary authority by district
engineers.
This general condition is adopted as
proposed.
GC 9. Management of Water Flows.
We proposed to modify this general
condition by simplifying the language to
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require that permittees maintain the preconstruction course, condition,
capacity, and location of open waters to
the maximum extent practicable.
Exceptions to this requirement may be
made if the primary purpose of the NWP
activity is to impound water or if the
activity benefits the aquatic
environment.
One commenter supported the
proposed modification. One commenter
supported the specific exception for
impoundment activities, and two
commenters supported the language that
allows stream modifications if there are
positive benefits to aquatic resources,
such as for stream restoration projects.
Two commenters supported the
language requiring compliance only to
the maximum extent practicable. One
commenter said that the practicability
considerations in this general condition
should take into account sound
engineering practices and project
economics.
The term ‘‘practicable’’ is defined in
the ‘‘Definitions’’ section of the NWPs.
Costs, as well as existing technology and
logistics, are considered when making
practicability determinations.
One commenter stated that this
general condition should not apply to
ephemeral streams. One commenter said
that this general condition should be
modified to prohibit dewatering
between October 1 and March 31 to
protect hibernating species in the
substrate of waterbodies. Another
commenter requested that the general
condition retain language stating that
detailed studies or monitoring would
not be required to ensure compliance,
and that the Corps would normally
defer to local and state officials on the
issue. Another commenter said that this
general condition provides only limited
value because it is qualitative and does
not require specific written
documentation and assurances
regarding how the requirements are met.
One commenter stated the requirements
of this general condition are
inappropriate and hazardous with
respect to regulation of stormwater
management facilities. One commenter
said that this general condition should
require NWP activities to accommodate
the passage of large woody debris and
stream bed load, especially for stream
crossing projects.
This requirement must apply to
ephemeral streams, because they may
carry substantial flow during storm
events. Time-of-year restrictions on
dewatering activities are more
appropriately addressed through the
regional conditioning process or
through special conditions added to
NWP authorizations by district
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engineers. We do not believe it is
necessary to retain language stating that
detailed studies or monitoring are not
required to ensure compliance with this
general condition, though it is not our
intent to require such studies where
compliance can be based on reasonable
assumptions about flow. District
engineers will use their judgment to
determine whether a particular activity
complies with this general condition. In
order to ensure that this general
condition does not unduly restrict the
construction and maintenance of storm
water management activities, we have
clarified that it does not apply to
activities that have a primary purpose of
managing storm water flows. The issue
of maintaining passage of large woody
debris in streams is more appropriately
addressed through regional conditions,
in areas where changes to the movement
of large woody debris may result in
more than minimal adverse effects on
the aquatic environment. Compliance
with the requirements of this general
condition will generally accommodate
the movement of bed load along a
stream channel.
This general condition is adopted as
proposed.
GC 10. Fills Within 100–Year
Floodplains. We proposed to modify
this general condition by simply
requiring permittees to comply with
applicable state or local floodplain
management requirements that have
been approved by the Federal
Emergency Management Agency
(FEMA).
Several commenters supported the
general condition. One commenter said
that the proposed change may cause a
slight increase in case-by-case review
and assertion of discretionary authority.
This commenter also requested that the
Corps provide guidance to assure
consistent implementation of this
general condition. A number of
commenters stated that local
governments are better able to
implement the FEMA program. Two
commenters favored the proposed
change because it avoids duplication
with other regulatory agencies, and
another commenter stated that it is a
simple and straightforward requirement.
One commenter said that the general
condition will create an incentive to
design projects that reduce impacts to
waters of the United States to qualify for
an expedited NWP authorization.
We do not agree that this general
condition will increase case-by-case
reviews and the number of times
discretionary authority is exercised. The
version of this general condition that
was adopted in 2002 prohibited the use
of NWPs 39, 40, 42, and 44 to authorize
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permanent, above-grade fills in waters
of the United States within mapped
floodways. Those activities required
authorization by regional general
permits or individual permits. The
general condition adopted today allows
those activities to be authorized by
NWP, provided the activities comply
with applicable state and local
floodplain management requirements
and the district engineer determines,
after reviewing the pre-construction
notification, that the individual and
cumulative adverse effects on the
aquatic environment and other public
interest review factors are minimal. We
continue to support efforts that reduce
duplication with other agencies.
Many commenters objected to the
general condition and requested that the
Corps retain the previous floodplain
prohibitions for NWPs 39, 40, 42 and
44. They said that the Corps has an
independent obligation and role in
protecting waters of the United States.
One commenter stated no fills should be
permitted within the 100-year
floodplain in specific watersheds. One
commenter said that employing the use
of discretionary authority on a case-bycase basis will produce uncertainty for
prospective permittees.
We do not believe it is appropriate to
use the Section 404 program to restrict
activities in flood plains over and above
the requirements of FEMA-approved
state and local floodplain management
programs, except in specific cases where
the district engineer determines that an
activity would result in more than
minimal adverse effects. This general
condition, in conjunction with reviews
of pre-construction notifications, will
provide sufficient protection to
floodplain values that is appropriate to
the scope of the Corps regulatory
authorities and implementing
regulations. This general condition will
also support the application of FEMAapproved state or local floodplain
management requirements that are
established to reduce flood hazards.
Restricting or prohibiting development
of 100-year floodplains is more
appropriately addressed through the
land use planning and zoning
authorities granted to state and local
governments. The Corps considers
impacts to floodplains and flood
hazards during its review of preconstruction notifications. If the
proposed activity will result in more
than minimal adverse effects to
floodplains or increases in flood
hazards, the district engineer will
exercise discretionary authority and
require an individual permit for the
proposed activity.
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We disagree that the pre-construction
notification review process will produce
more uncertainty for permittees. If the
proposed work will have minimal
adverse effects on the aquatic
environment and other public interest
review factors, such as floodplain values
and flood hazards, the activity can be
authorized by the applicable NWP. One
benefit of the modified general
condition is that it applies to all NWP
activities, not just NWPs 39, 40, 42, and
44.
One commenter indicated that FEMA
regulations are only designed to assure
development is reasonably safe from
flooding not to protect the quality and
quantity of downstream waterways or
the aquatic resources associated with
the floodplain and downstream water
segments. Two commenters stated that
floodplain managers will not receive
pre-construction notifications and
therefore they will not be aware of
floodplain development activities
because they will no longer receive
public notices for these individual
permits. Two commenters said that the
National Flood Insurance Program
standards are insufficient to minimize
flood hazard and floodplain impacts.
One commenter argued that the Corps
should strengthen and not weaken the
floodplain protections that are outlined
in 33 CFR 320.4(l)(2) and Executive
Order 11988, Floodplain Management.
One commenter concluded that the
NWPs will have more than minimal
impacts because of the proposed
modification of this general condition.
When reviewing pre-construction
notifications, district engineers will
assess adverse effects to the aquatic
environment, including impacts to
aquatic resources located within 100year floodplains and downstream
waterways. General condition 9 requires
permittees, to maintain to the maximum
extent practicable, the pre-construction
course, condition, capacity, and location
of open waters. State water quality
certifications ensure that NWPs do not
authorize activities that degrade
downstream water quality. Floodplain
development activities are already
thoroughly reviewed by state and local
governments under their planning and
zoning authorities, especially in those
floodplains that consist mostly of
uplands, where development is more
likely to occur. The Federal Emergency
Management Agency is designated
through E.O. 11988 as the lead Federal
agency for floodplain management, and
we are deferring to their program
requirements for floodplain
management. The proposed
modification of this general condition
complies with 33 CFR 320.4(l)(2). The
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modification of this general condition
will not cause the NWP program to
result in more than minimal individual
and cumulative adverse environmental
effects.
One commenter said that this general
condition should be modified to require
documentation of compliance with
FEMA minimum standards by a
licensed professional engineer, and
require consultation with resource
agencies. One commenter suggested
modifying this general condition to
require prospective permittees to
demonstrate they have applied the
National Environmental Policy Act
process and to justify ‘‘no reasonable
option’’ exists before filling within the
base floodplain. One commenter noted
that not all floodplains have been
mapped and as such they do not fall
under authority of a local government.
Two commenters requested clarification
on how the general condition will be
applied when a 100-year floodplain is
identified by an engineering study but
FEMA approved management
requirements are absent.
Requiring documentation of
compliance with FEMA-approved
standards is unnecessary for the
purposes of the NWPs, because such
requirements are more appropriately
addressed through state and local
construction authorizations. If a
separate National Environmental Policy
Act process is applicable for a particular
development activity, then the lead
Federal agency will conduct that
process. For the purposes of the NWPs,
compliance with the National
Environmental Policy Act is achieved
through the decision documents issued
for each NWP. This general condition
does not apply to 100-year floodplains
where FEMA-approved state or local
floodplain management requirements
have not been established. In general,
such floodplains have not been mapped.
In such areas, district engineers will
review pre-construction notifications
and assess the adverse effects on
floodplains and flood hazards to the
extent practicable, and add special
conditions as appropriate.
Two commenters requested
clarification of the mechanism and
documentation necessary to complete
the public interest evaluation. One
commenter asked if this process is
expected to increase the amount of time
needed to complete the review of a preconstruction notification.
The general condition simply requires
permittees to comply with applicable
FEMA-approved state or local
floodplain management requirements. It
does not require separate
documentation to be provided to the
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district engineer with a pre-construction
notification. The modification of this
general condition is not expected to
cause an increase in the amount of time
to prepare or review a pre-construction
notification.
This general condition is adopted as
proposed.
GC 11. Equipment. We proposed to
modify the general condition to include
mudflats, in addition to wetlands.
One commenter suggested changing
this general condition to require heavy
equipment to provide low ground
pressure, to further minimize soil
disturbance.
We do not agree that this change is
necessary, because the general condition
states that other measures can be used
to minimize soil disturbance. This
general condition is adopted as
proposed.
GC 12. Soil Erosion and Sediment
Controls. We did not propose any
changes to this general condition.
One commenter expressed support for
this general condition, stating that it
provides sufficient flexibility to address
emergency situations, public safety or
infrastructure repairs, or situations
where it is necessary to work in higher
water conditions in order to adjust
restoration design to meet on-site
hydrologic and fluvial geomorphic
conditions. One commenter said that
the term ‘‘low-flow’’ is not adequately
defined, and therefore it provides
inadequate protection of the aquatic
environment. One commenter suggested
modifying this general condition to
require permittees to follow state and/or
local storm water sediment control
requirements.
Determinations of low-flow
conditions will be made by district
engineers on a case-by-case basis. We
believe the condition provides sufficient
protection for the aquatic environment.
Appropriate soil erosion and sediment
control measures may be established by
different levels of government or
different agencies, so it would be more
effective to retain the present language.
Such requirements are independently
applicable in any case.
This general condition is adopted as
proposed.
GC 13. Removal of Temporary Fills.
We proposed to modify this general
condition by replacing the phrase ‘‘their
preexisting elevation’’ with ‘‘preconstruction conditions.’’
One commenter supported the
proposed change. Four commenters
objected to the proposed change, stating
that the language implies that the site
needs to be revegetated or mitigated.
One commenter suggested defining
‘‘temporary’’ as less than six months.
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One commenter recommended
modifying the text of this general
condition to recommend removal of
temporary fills during dewatered or
low-flow conditions. Another
commenter said that this general
condition should require filled areas to
be restored, as much as possible, to the
same elevation, contours, grade,
substrate, vegetative composition,
hydrology, and/or geomorphology.
We agree that the proposed
modification can be difficult to
implement and enforce. For example,
the proposed language implies that to
return an area inhabited by trees to its
pre-construction conditions, trees
would have to be planted. Therefore, we
have changed the phrase ‘‘preconstruction conditions’’ to ‘‘preconstruction elevations’’ to require that
the permittee return the affected area to
its previous elevations. We have also
added a new sentence that requires the
permittee to revegetate the affected area,
as appropriate. A temporarily filled area
that was previously vegetated must be
planted with appropriate plant materials
and allowed to grow back after the
temporary fill is removed and the preconstruction elevations restored. In
some cases, such as stream channels, it
may be sufficient to simply remove
temporary fills to satisfy this general
condition.
The general condition is adopted with
the modifications discussed above.
GC 14. Proper Maintenance. We did
not propose any changes to this general
condition.
One commenter stated the Corps
should require that a new stream
crossing be constructed when a crossing
requires two or more debris removal
requests within 10 years. One
commenter said that the general
condition should be modified to require
maintenance as necessary to ensure
minimal impacts and public safety. One
commenter stated that long-term
maintenance of structures and/or fills
should be evaluated during the permit
process and authorized in the permit
authorizing construction.
We disagree with these suggested
changes. We cannot condition the NWPs
to require a permittee to install a new
stream crossing if debris accumulates at
a certain frequency. Activities
authorized by NWPs must already result
in minimal adverse effects on the
aquatic environment, and it is not
necessary to add such a requirement to
this general condition. Maintenance of
authorized activities may be conducted
either under the Clean Water Act
exemption at Section 404(f)(1)(B) or
under NWPs 3, 31, or 35.
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The general condition is adopted as
proposed.
GC 15. Wild and Scenic Rivers. We
did not propose any changes to this
general condition.
One commenter recommended
expanding the prohibition to state wild
and scenic and recreational river
systems, and to any activities in rivers
subject to the review of the National
Park Service. One commenter expressed
support for the general condition and
recommended it be modified to require
that the Federal agency with direct
management responsibility for the river
be contacted regarding the proposed use
of an NWP and that the Corps receive
a written statement from that agency
regarding the effects the activity will
have on the river.
State wild and scenic rivers are more
appropriately addressed through state
laws, regulations, and programs. The
general condition contains language
requiring the appropriate Federal
agency with direct management
responsibility for the river to determine
in writing that the proposed activity
will not adversely affect that river’s
designation. The Corps will not issue an
NWP verification for an activity in a
National Wild and Scenic River without
the appropriate documentation.
This general condition is adopted
without change.
GC 16. Tribal Rights. We did not
propose any changes to this general
condition. One commenter asked how
the Corps will determine whether tribal
rights are impacted, and if a tribal right
is impaired.
We cannot define a specific threshold
to be used to determine compliance
with this general condition. District
engineers make these determinations on
a case-by-case basis, through
appropriate consultations with Indian
tribes.
This general condition is adopted
without change.
GC 17. Endangered Species. We
proposed to modify this general
condition by stating that no activity is
authorized by NWP, if it ‘‘may affect’’ a
listed species or critical habitat unless
Section 7 consultation has been
completed. We also proposed to state
that district engineers will make ‘‘may
affect’’ or ‘‘no effect’’ determinations
and notify prospective permittees
within 45 days of receipt of a complete
pre-construction notification.
Several commenters supported the
proposed modifications of this general
condition. One commenter
recommended specifying the
documentation that should be submitted
with the pre-construction notification in
circumstances when no listed species or
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critical habitat will be affected. Two
commenters requested that the 45 day
time limit for notifying applicants of an
effect determination be reduced to 30
days. One commenter requested
clarification on whether the Corps has
45 days from submittal of the preconstruction notification or 45 days
from receipt of a complete application,
to notify the applicant of a ‘‘may effect’’
determination, and whether this will
result in extra time to complete an
NWP.
This general condition specifies that
permittees shall notify the Corps if any
listed species or critical habitat might be
affected or is in the vicinity of the
project. If this does not apply, no
additional information is required to be
submitted. We believe that 45 days is a
reasonable and practical deadline, and it
is consistent with the pre-construction
notification time frame. The general
condition states that the Corps will
notify the applicant within 45 days of
receipt of a complete pre-construction
notification. However, if the applicant
has provided notification to the Corps of
possible effects on listed species or
critical habitat, the applicant must wait
for a Corps determination of either ‘‘may
affect’’ or ‘‘no effect’’, even if this takes
more than 45 days.
Several commenters expressed
concern that requirement for Section 7
consultation in the absence of a ‘‘no
effect’’ determination would delay
processing of pre-construction
notifications, and that the requirement
to wait for the Corps ‘‘no effect’’
determination increases the
administrative burden and uncertainty
for applicants. Several commenters
recommended that, if an applicant does
not hear from the Corps within 45 days,
the applicant may treat the lack of
response as a ‘‘no effect’’ determination
and proceed with the NWP activity.
Other commenters stated that the openended period for the Corps to resolve
concerns about species could result in
NWPs taking much longer to issue than
45 days.
The 45-day period is necessary to
allow district engineers to review
proposed NWP activities that require
notification because federally-listed
species or critical habitat might be
affected or are in the vicinity of the
project (see 33 CFR 330.4(f)(2)). During
that 45 day period, the district engineer
will determine if the proposed project
will have ‘‘no effect’’ or ‘‘may affect’’
listed species or critical habitat. If the
proposed activity may affect listed
species or critical habitat, the
prospective permittee cannot begin the
activity until the Endangered Species
Act requirements have been satisfied,
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even if 45 days have passed since the
district received a complete preconstruction notification. Many ‘‘no
effect’’ determinations do not take the
full 45 days. We acknowledge that some
NWP verification requests may take
longer than 45 days, but the Corps is
legally obligated to comply with the
Endangered Species Act. The ESA
requires Section 7 consultation for any
activity authorized by a Federal agency
unless that agency determines that the
activity will have ‘‘no effect’’ on listed
species. In cases where the permittee
has determined that no listed species or
critical habitat are in the vicinity of the
project or might be affected by it, and
thus has not notified the Corps of any
possible effects, then (but only in such
cases) the permittee does not have to
wait for further confirmation of ESA
compliance from the Corps.
One commenter stated that the
wording in the general condition differs
from that in the Endangered Species Act
and in the existing NWPs, as it applies
the standard of ‘‘may affect’’ rather than
‘‘takings’’ of listed species. In addition,
without clear guidance, the ‘‘may effect’’
standard is likely to be applied
inconsistently from district to district.
Section 7 of the Endangered Species
Act states that Federal agencies must
consult with the U.S. Fish and Wildlife
Service or the National Marine Fisheries
Service if an activity ‘‘may affect’’ listed
species or habitat. This language is
virtually the same as that in the 2002
NWPs, including the requirement that a
permittee cannot begin work until
notified by the Corps if the project
might affect a listed species or critical
habitat.
One commenter recommended
clarification of the terms ‘‘might be
affected’’ and ‘‘may affect’’.
As stated in the text of the general
condition, the district engineer
determines if an activity ‘‘may affect’’
listed species or critical habitat. A nonfederal permittee must notify the district
engineer if listed species or critical
habitat might be affected, so the district
engineer can determine if the activity
‘‘may affect’’ the habitat or species. We
have modified the second sentence of
paragraph (b) of this general condition
by changing the word ‘‘may’’ to ‘‘might’’
in order to clearly distinguish the formal
determination by the Corps (‘‘may
affect’’ or ‘‘no effect’’) from the
requirement on the applicant to notify
the Corps where there is sufficient cause
for concern to warrant a formal
determination. This requirement applies
if habitat or species is in the vicinity of
the project or might be affected by it, or
if the project is located in the habitat.
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One commenter recommended
modifying this general condition to
exempt activities that occur in the
vicinity of free-swimming species from
the pre-construction notification
requirement, provided the activities
include reasonable efforts to avoid
physical contact with listed species.
Any time a proposed NWP activity
has the potential to affect listed species
or critical habitat, the Corps must
evaluate it and make a ‘‘no effect’’ or
‘‘may affect’’ determination. This
requirement cannot be waived for freeswimming species, although efforts
taken to avoid physical contact with
listed species might result in a
determination that the activity will have
‘‘no effect’’ on that species. Even in the
case of a ‘‘may effect’’ determination,
such efforts may help to expedite
Section 7 consultation with the
Services.
One commenter suggested clarifying
that the work or activities that are
prohibited from commencing until the
Corps has provided notification of
compliance with the Endangered
Species Act only refers to work in
waters of the United States, not upland
areas. Several commenters stated that
language requiring applicants to notify
the Corps if listed species or habitat is
in the ‘‘vicinity’’ of the activity creates
uncertainty and should be eliminated.
District engineers must evaluate
effects on listed species or habitat of any
activity that is within the Corps’ scope
of analysis under the Endangered
Species Act. This might include some
areas outside of waters of the United
States. However, it is correct that a
Section 404 permit is only required for
discharges of dredged or fill material
into waters of the United States. The
Corps has no authority to prohibit
activities that do not involve such
discharges. However, an activity in an
upland area that adversely affects a
listed species may make it more difficult
for the Corps to later determine that an
associated discharge of dredged or fill
material into waters of the United States
has ‘‘no effect’’ and/or may complicate
any Section 7 consultation that is
subsequently required. While defining
the ‘‘vicinity’’ of an activity might be
difficult, the Corps believes it must
retain the ability to evaluate the effects
of projects on species that are nearby,
mobile, or otherwise could be affected.
Defining the appropriate vicinity will
also depend on the natural history of the
particular species. If there is any doubt,
permittees should contact the Corps or
the local office of the USFWS or NMFS
for guidance.
A couple of commenters stated that,
as the U.S. Fish and Wildlife Service is
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allowed to comment on coal mine
permit applications during the Surface
Mining Control and Reclamation Act
(SMCRA) process, there is no need for
consultation associated with Corps
permits for coal mining.
Section 7(a)(2) of the Endangered
Species Act requires Federal agencies to
consult with the Services to ensure that
they are not undertaking, funding,
permitting, or authorizing actions likely
to jeopardize the continued existence of
listed species or destroy or adversely
modify designated critical habitat. This
responsibility cannot be waived, unless
another Federal agency is the lead
agency for the project and conducts the
required consultation. In cases where
SMCRA is administered by a state
agency, the Corps is required to conduct
the necessary Federal consultation.
Information obtained during other
environmental reviews, including any
comments made by the Services during
the SMCRA process, is used by the
Corps in evaluating the NWP.
One commenter stated that neither
applicants nor the Corps are adequately
trained to make endangered species
determinations and therefore the Corps
should institute formal consultation for
each proposed NWP activity. In
addition, pre-construction notification
thresholds should be eliminated or
reduced so that applicants are not put
in the position of deciding whether or
not their project has impacts on
protected species.
Section 7 consultation is a
cooperative effort involving affected
parties engaged in analyzing effects
posed by proposed actions on listed
species or critical habitat(s). Many NWP
activities result in ‘‘no effect’’ to listed
species or critical habitat, so it is not
necessary to conduct formal
consultation for each NWP activity. The
determination of jeopardy/no jeopardy
is based on a careful analysis of the best
available scientific and commercial
data. The Corps is engaging with the
Services on programmatic Section 7
consultation for the NWPs, but projectspecific evaluations and consultation
are still required to ensure that
permitted activities do not jeopardize
the continued existence of a listed
species or critical habitat. The preconstruction notification thresholds for
NWPs provide a balance between
efficient authorization of activities that
have minimal adverse environmental
impact, and environmental protection,
including protection of listed species
and critical habitat. The requirement for
prospective permittees to notify the
district engineer if a listed species or
critical habitat might be affected or is in
the vicinity of the project provides a
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relatively low bar for notification to the
Corps of potential effects, while not
bogging down the NWP process in cases
where the applicant has performed due
diligence and determined that there are
no listed species or critical habitat in
the vicinity of the project.
One commenter recommended that
the general condition specify that the
U.S. Fish and Wildlife Service or
National Marine Fisheries Service has to
make jeopardy determinations and that
the Corps will initiate any required
Section 7 consultation within 45 days of
receiving a complete pre-construction
notification.
We do not agree that it is necessary
to modify this general condition to state
that the U.S. Fish and Wildlife Service
or National Marine Fisheries Service
will make jeopardy determinations.
Those determinations will be made
when they issue biological opinions in
response to a request for Section 7
consultation. The purpose of this
general condition is to ensure
compliance with the requirements of the
Endangered Species Act, and to provide
timely notification to prospective
permittees, so that they do not begin
work until the requirements of Section
7 have been fulfilled.
One commenter recommended that
the prohibition on activities that
adversely affect federally listed species
should also apply to official state-listed
endangered or threatened species.
The Endangered Species Act only
applies to Federally-listed species.
States may impose their own
restrictions or prohibitions on activities
that affect state-listed species.
One commenter suggested adding the
word ‘‘negatively’’ to the second
sentence of paragraph (a), to limit it to
those activities that may negatively
affect listed species or critical habitat.
One commenter stated that this general
condition should not apply to shellfish
seeding activities authorized by NWPs
27 or 48, since traditional shellfish
seeding activities do not negatively
affect listed species or their habitat.
The term ‘‘may affect’’ comes from the
ESA and is the statutory criterion for
determining when Section 7
consultation is required. Changing this
language to only apply to negative
effects would not be consistent with the
Corps’ responsibilities under the
Endangered Species Act. The general
condition applies to all NWPs, to the
extent that they have the potential to
affect listed species or critical habitat. If
an activity would not have an affect on
listed species, no Section 7 consultation
is required. The notification
requirements in this general condition
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facilitate the Corps’ compliance with its
Section 7 obligations.
One commenter stated that many
activities eligible for NWPs are covered
under programmatic Section 7
consultations. Therefore, it should be
clarified that if a project falls within the
scope of a program that has been
reviewed and approved under Section 7
consultation, then individual
consultation is not required. One
commenter recommended modifying
this general condition to clarify the
responsibilities of Federal permittees
that use the NWPs.
If Section 7 consultation has been
completed for an activity, either
programmatically or individually, the
activity can be authorized under NWPs.
This is implied in the statement that
‘‘no activity is authorized under any
NWP which ‘‘may affect’’ a listed
species or critical habitat, unless
Section 7 consultation addressing the
effects of the proposed activity has been
completed.’’ We do not believe
additional clarification is necessary.
When submitting a pre-construction
notification for an activity that may
affect a listed species, the applicant
should indicate if Section 7 consultation
has already been conducted, the Federal
agency conducting the consultation, and
the outcome of the consultation.
We have added a new paragraph to
this general condition (paragraph (b)), to
clarify that Federal agencies are to
follow their own procedures for
complying with the requirements of the
Endangered Species Act, which is
consistent with 33 CFR 330.4(f)(1). This
paragraph also requires Federal
permittees to provide appropriate
documentation to the district engineer
to demonstrate compliance with those
requirements.
This general condition is adopted,
with the modifications discussed above.
GC 18. Historic Properties. We
proposed to modify this general
condition by removing the reference to
Appendix C of 33 CFR part 325 and
stating that the district engineer will
comply with the current procedures for
addressing the requirements of Section
106 of the National Historic
Preservation Act. We also proposed to
modify the general condition to state
that district engineers will notify
prospective permittees within 45 days
of receipt of a complete pre-construction
notification whether section 106
consultation is required.
One commenter agreed with the 45day timeline for a Corps response. One
commenter stated that the general
condition should specify what
documentation should be submitted
with the pre-construction notification.
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One commenter stated that it should be
the applicant’s responsibility, not the
Corps’, to find out if section 106
consultation is required.
The general condition states that, for
activities that may have the potential to
cause an effect on listed, eligible, or
potentially eligible properties, the preconstruction notification must state
which historic properties may be
affected by the proposed work or
include a map indicating the location of
the project and the location of the
historic properties. The Corps is
responsible for making determinations
and findings for the purposes of section
106. We have modified paragraph (a) of
this general condition to clarify that
NWP activities are not authorized until
the requirements of section 106 have
been satisfied, in cases where the
district engineer determines that the
NWP activity has the potential to cause
an effect on a historic property. If the
applicant has provided notification to
the Corps of possible effects on historic
properties the applicant must wait for a
Corps determination of either ‘‘potential
to cause effects’’ or ‘‘no potential to
cause effects’’ even if this takes longer
than 45 days.
Several commenters expressed
concerns about the delay in NWP
authorization resulting from the 45-day
requirement and suggested that
authorization be automatically granted
if the Corps does not notify the
applicant within 45 days.
The 45 day period is necessary to
allow district engineers to adequately
review those activities that may affect
eligible properties. During that 45 day
period, the district engineer will
determine if the proposed project has
the potential to cause effects on historic
properties. If so, the prospective
permittee cannot begin the activity until
section 106 consultation has been
completed, even if 45 days has passed
since the district received a complete
pre-construction notification (see 33
CFR 330.4(g)(2)). However, many
determinations do not take the full 45
days. The Corps cannot waive section
106 compliance by allowing the
applicant to assume ‘‘no potential to
cause effects’’ if the Corps has not been
able to respond within 45 days.
Therefore, this provision has not been
changed. In cases where the permittee
has determined there are no historic
properties for which the activity has the
potential to cause effects, and has thus
not notified the Corps of such properties
(but only in such cases) the permittee
does not have to wait for further
confirmation of NHPA compliance from
the Corps.
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One commenter stated that the Corps
should eliminate the language that
requires an applicant to notify the Corps
if an activity may affect any property
which the ‘‘prospective permittee has
reason to believe may be eligible for
listing,’’ as the Corps is required only to
take into account the effect of an
undertaking on property that is
included in or eligible for inclusion in
the National Register. Two commenters
recommended modifying this general
condition to require a preliminary
survey of the project area for the
purposes of section 106 compliance.
The purpose of the notification
requirement in this general condition is
to provide the district engineer with the
opportunity to consider effects to
historic properties, in cases where preconstruction notification is not required
by the NWP itself. Since the definition
of ‘‘historic property’’ includes
properties that are eligible for listing in
the National Register of Historic Places,
and the Federal agencies are required to
carry out appropriate identification
efforts, we believe that the concept in
the proposed general condition is
appropriate. We have modified this
paragraph to provide further
clarification of the role of the nonFederal permittee, and have added a
sentence that states that district
engineers are responsible for making
final effect determinations. The
notification requirement helps the Corps
carry out those identification efforts. We
have included a sentence in paragraph
(c) to clarify that district engineers are
to make reasonable and good faith
efforts to identify historic properties
when reviewing proposed NWP
activities. We do not believe it is
necessary to require a preliminary
survey of the project area with the preconstruction notification. District
engineers will review available
information to determine if further
investigations are warranted for section
106 compliance.
One commenter recommended that
programmatic consultation and
agreements should be allowed for
section 106. One commenter stated that
the Corps should initiate programmatic
consultation on each NWP before
reissuing them.
Programmatic agreements conducted
in accordance with 36 CFR 800.14(b),
meet the requirements of this general
condition. We do not believe
programmatic consultation on each
NWP in advance is necessary or
practical. Consultation will be
conducted as appropriate for all
activities that may affect historic
properties listed on, eligible, or
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potentially eligible for listing in the
National Register of Historic Places.
One commenter suggested clarifying
that the work or activities that are
prohibited from commencing until the
Corps has provided notification of
compliance with section 106 only refers
to work in waters of the United States,
not upland areas outside of this area.
One commenter stated that this general
condition shifts the burden of
determining ‘‘no effect’’ on historic
properties from applicants and the
Corps to other agencies, which could
delay authorization. One commenter
recommended modifying this general
condition to clarify the responsibilities
of Federal permittees that use the
NWPs.
District engineers must evaluate
effects on eligible historic properties
that are within the Corps’ scope of
analysis under section 106. This might
include some areas outside of waters of
the United States. However, it is correct
that a Section 404 permit is only
required for discharges of dredged or fill
material into waters of the United
States. The Corps has no authority to
prohibit activities that do not involve
such discharges. However, an activity in
an upland area that adversely affects a
historic property may make it more
difficult for the Corps to later determine
that a Section 106 consultation is not
required for an associated discharge of
dredged or fill material into waters of
the United States, and/or may
complicate any Section 106 consultation
that is subsequently required. The
district engineer is responsible for
making determinations and findings
under section 106. This process has not
changed. We have added a new
paragraph (b) to this general condition,
which states that Federal permittees
should follow their own procedures for
complying with the requirements of
section 106.
One commenter expressed concerns
that the general condition lacks clarity
about who is responsible for
identification and evaluation of historic
properties and determination of effects,
how such identification will be
accomplished, and the nature of
consultation required. This commenter
suggested revised wording for the
general condition and recommended
that the Corps include a definition for
historic properties. We agree that the
wording proposed by this commenter
clarifies responsibilities and procedures
and have revised the general condition
accordingly. We have also added a
definition for historic property in the
‘‘Definitions’’ section for the NWPs.
This commenter also noted that the
Corps’’ historic properties regulations
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are not consistent with Advisory
Council on Historic Preservation’s
regulations at 36 CFR part 800 and are
not approved by the Council. As noted
by the commenter, the Corps and the
Council are currently involved in
discussions to resolve the differences
between the Corps’ procedures and the
Council’s regulations at 36 CFR part
800. Pending the outcome of those
discussions, the reference in this general
condition to the Corps current
procedures means the Corps ‘‘Revised
Interim Guidance for Implementing
Appendix C of 33 CFR Part 325 with the
Revised Advisory Council on Historic
Preservation’s Regulations at 36 CFR
Part 800’’ dated April 25, 2005.
The use of the interim guidance, as
well as the Corps Regulatory Program
procedures for the protection of historic
properties at Appendix C of 33 CFR Part
325, are provisional measures to comply
with the requirements of Section 106 of
the National Historic Preservation Act
until updated alternative procedures
that are tailored to the Corps Regulatory
Program can be promulgated through
the appropriate processes.
This general condition is adopted
with the modifications discussed above.
GC 19. Designated Critical Resource
Waters. We proposed to modify this
general condition to eliminate
provisions that duplicate the
requirements of other general
conditions.
One commenter recommended adding
proposed NWPs E and F to paragraph (a)
of this general condition, to prohibit the
use of those permits to authorize
discharges of dredged or fill material in
waters of the United States for activities
in, or directly affecting, critical resource
waters.
We have modified paragraph (a) of
this general condition to include NWPs
E and F (now designated as NWPs 49
and 50), since those activities have the
potential to result in more than minimal
adverse effects to designated critical
resource waters and their adjacent
wetlands. These mining activities may
be authorized by individual permits or
regional general permits in these waters.
One commenter stated that the Corps
should not prohibit the use of an NWP
in critical resource waters if the agency
managing those critical resource waters
approves those activities. This
commenter recommended requiring preconstruction notification for all
activities in critical resource waters and
conducting coordination with the
managing agency. Another commenter
stated that limiting the use of NWPs in
designated critical resource waters
should be done through regional
conditions and coordination with state
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and local agencies and resource
agencies, instead of a general condition.
Paragraph (a) of this general condition
lists those NWPs that have a greater
potential to result in more than minimal
adverse effects on the aquatic
environment, if they involve discharges
of dredged or fill material into those
designated critical resource waters, or
their adjacent wetlands. Therefore, it
would be more appropriate to review
those activities through the individual
permit process, with agency
coordination, or authorize those
activities through regional general
permits. The designated critical
resource waters listed in this general
condition are generally considered to be
important to the national public
interest. Proposed activities involving
discharges of dredged or fill material
into those waters and their adjacent
wetlands warrant more thorough
review, through either the preconstruction notification process or
other forms of Department of the Army
authorization, such as individual
permits.
One commenter suggested that in
order to provide consistency with state
definitions, a definition for ‘‘natural
heritage sites’’ should be included in the
text of this general condition.
Natural heritage sites are defined and
designated by state agencies. The
criteria and processes for designating
state natural heritage sites vary from
state to state. District engineers will
utilize the appropriate state
designations when implementing this
general condition. Therefore, we do not
believe that it is appropriate to provide
a definition of state natural heritage
sites at the national level.
One commenter suggested that source
waters used for drinking water or
ground water recharge should be
included in the definition of critical
resource water. The same commenter
suggested that there should be no
provision for the use of discretionary
authority regarding discharges of
dredged or fill material into designated
critical waters.
Concerns regarding impacts to sources
for drinking water and ground water
recharge are more appropriately
addressed through regional conditioning
of the NWPs or review of preconstruction notifications for specific
and identified waters. Division
engineers can regionally condition the
NWPs to prohibit or limit their use in
such high value waters. District
engineers will exercise discretionary
authority and require individual permits
for activities proposed in high value
waters that will result in more than
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minimal adverse effects on the aquatic
environment.
One commenter said that critical
resource waters should include the
following areas: watersheds of
nationally-designated wild and scenic
rivers, waters within wilderness areas,
national parks and wildlife refuges, and
all waters with similar state
designations. Another commenter
recommended adding waters designated
as National Monuments and National
Historic Sites to the categories of waters
in this general condition. This
commenter also said that vernal pools,
bogs and fens, native wet prairie,
forested wetlands, eelgrass beds, and
coral reefs should also be considered as
designated critical resource waters
subject to this general condition.
The use of NWPs in components of
the National Wild and Scenic River
System or designated study rivers is
addressed by general condition 15, Wild
and Scenic Rivers. Restricting or
prohibiting the use of NWPs in waters
of the United States within wilderness
areas, national parks, national
monuments, national historic sites,
national wildlife refuges, or statedesignated wilderness, parks, or refuges,
is more appropriately addressed through
the regional conditioning process. In
areas where vernal pools, bogs and fens,
native wet prairie, forested wetlands,
eelgrass beds, and coral reefs warrant
greater levels of protection, division
engineers may impose regional
conditions on NWPs to restrict or
prohibit their use in those waters.
Division engineers will determine
whether regional conditions are
necessary to ensure that the NWPs
authorize only activities resulting in
minimal individual and cumulative
adverse effects on the aquatic
environment in those areas.
This general condition is adopted
with the modification discussed above.
GC 20. Mitigation. We proposed
several modifications to this general
condition, such as requiring
compensatory mitigation for NWP
activities that require a pre-construction
notification and result in the loss of
greater than 1⁄10 acre of wetlands. We
also proposed to add a provision stating
that compensatory mitigation may be
required for activities that result in
permanent adverse effects to certain
aquatic resource functions and services.
Several commenters requested
clarification as to whether
compensatory mitigation is required
only for permanent losses of waters of
the United States, or whether it is also
required for temporary impacts to those
waters. A commenter asked if
compensatory mitigation for stream bed
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impacts should be quantified as linear
feet or acres. A couple of commenters
said that district engineers should be
able to require compensatory mitigation
for losses of other types of waters of the
United States, such as streams. One
commenter expressed support for
watershed-based compensatory
mitigation. One commenter said that it
was unclear how the proposed
compensatory mitigation rule published
in the March 28, 2006, issue of the
Federal Register (71 FR 15520) would
apply to the NWP program. One
commenter said that preservation
should not be used as compensatory
mitigation.
Compensatory mitigation is required
only for permanent losses of waters of
the United States, or for permanent
adverse effects to aquatic resource
functions (such as those described in
paragraph (h) of this general condition).
The restoration of waters of the United
States where there were temporary fills
and other impacts during the
construction activity is not considered
compensatory mitigation. Those actions
are addressed by general condition 13.
The unit of measure used to quantify
stream bed impacts and compensatory
mitigation is at the discretion of the
district engineer. Compensatory
mitigation may be required for losses of
streams and other types of waters of the
United States, to ensure that the NWP
activity results in minimal individual
and cumulative adverse effects on the
aquatic environment. To clarify this
concept, we have added a new
paragraph (d) to this general condition,
which states that the district engineer
may require compensatory mitigation
for losses of streams and other waters of
the United States. When a final
compensatory mitigation rule becomes
effective, it will apply to all types of
Department of the Army permits,
including the NWPs. We are in the
process of reviewing comments on the
proposed rule and developing the final
rule, in cooperation with the
Environmental Protection Agency.
Preservation of aquatic resources is an
important form of compensatory
mitigation which is appropriate in some
cases to protect and maintain aquatic
resource functions and services in the
watershed. All compensatory mitigation
should be determined, to the extent
practicable, using a watershed approach
that considers watershed needs
holistically and identifies locations and
types of compensatory mitigation that
will be most beneficial to the watershed.
Two commenters said that
prospective permittees should be
required to submit statements with
NWP pre-construction notifications that
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explain how avoidance and
minimization of losses of waters of the
United States was achieved. They said
that this statement would assist district
engineers in determining if avoidance
and minimization has been achieved to
the maximum extent practicable. One
commenter objected to including
temporary adverse effects in the
language in paragraph (a) of this general
condition, stating that it is contrary to
the definition of ‘‘loss of waters of the
United States’’ which refers only to
permanent losses. Another commenter
said that compensatory mitigation
should be considered only after
avoidance and minimization has
occurred.
We do not agree that it is necessary
to require an avoidance and
minimization statement with preconstruction notifications to evaluate
whether avoidance and minimization
has been achieved to the maximum
extent practicable on the project site.
The information required for a complete
pre-construction notification, including
any plans submitted with the preconstruction notification, is sufficient
for district engineers to determine
compliance with this general condition.
We believe the minimization of
temporary impacts to waters of the
United States is important for ensuring
that NWP activities result in minimal
adverse effects on the aquatic
environment, even though those
impacts do not result in permanent
losses and generally do not require
compensatory mitigation. The
requirements of this general condition
support the mitigation sequence of
avoidance, minimization, and
compensation. Compensatory mitigation
requirements are determined after
considering compliance with the
avoidance and minimization provisions
of this general condition.
Several commenters expressed
support for the 1⁄10 acre threshold for
requiring compensatory mitigation for
wetland losses that require preconstruction notification. A number of
commenters said that compensatory
mitigation should be required for all
wetland losses, because of the potential
cumulative impacts resulting from many
small wetland losses. Several
commenters asserted that there are
enough mitigation banks and in-lieu fee
programs throughout the country to
require compensatory mitigation for
wetland losses of less than 1⁄10 acre.
Two commenters recommended
changing the compensatory mitigation
threshold to 1⁄4 acre, and one commenter
reasoned that the threshold should be
higher because the NWP program
already meets the ‘‘no overall net loss’’
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goal for wetlands. Two commenters said
that there should not be a mandatory
compensatory mitigation requirement
for the NWPs. Compensatory mitigation
should be required only when necessary
to ensure minimal adverse effects.
We are retaining the 1⁄10 acre
compensatory mitigation threshold for
wetland losses, with the provision
allowing district engineers to waive this
requirement on a case-by-case basis if
the activity results in minimal adverse
effects on the aquatic environment. This
will help ensure that we continue to
achieve the ‘‘no overall net loss’’ goal
while providing appropriate flexibility
and transparency to the wetlands
compensatory mitigation requirements
for the NWPs. We do not believe it is
appropriate or practicable to require
compensatory mitigation for all
activities authorized by NWPs that
result in wetland losses. Even though
there are several hundred mitigation
banks and in-lieu fee programs in the
United States that are currently
operational, these mitigation banks and
in-lieu fee programs are not distributed
throughout the country in a manner that
would support the recommended
change to this general condition. In
many regions, individual permitteesponsored projects are the only option
available for compensatory mitigation to
offset losses authorized by NWP
activities. For very small impacts, such
projects may not be practicable. Because
most larger projects require more than
one-for-one compensation, we are
confident that we can continue to meet
the ‘‘no overall net loss’’ goal without
requiring mitigation for all impacts.
One commenter said that general
condition 20 is not consistent with 33
CFR 320.4(r)(2), which states that
compensatory mitigation will be for
significant resource losses. This
commenter articulated that there is large
difference between ‘‘no more than
minimal’’ and ‘‘significant resource
loss.’’ This commenter also stated that if
the proposed activity requires a preconstruction notification and will result
in loss of greater than 1⁄10 acre of
wetlands, but the activity will result in
minimal adverse effects, then
compensatory mitigation cannot be
required. This commenter
recommended removing the 1⁄10 acre
threshold, and modifying the general
condition to simply state that the
district engineer will require
compensatory mitigation when
necessary to ensure minimal individual
and cumulative adverse effects on the
aquatic environment.
General condition 20 is consistent
with the NWP regulations governing
mitigation (see 33 CFR 330.1(e)(3)). That
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regulation states that mitigation may be
required to reduce the adverse effects of
the NWP activity so that they are
minimal. There is already sufficient
flexibility in the general condition for
the district engineer to waive the
compensatory mitigation requirement
for wetland losses that exceed 1⁄10 acre
if the project impacts are minimal. We
believe the threshold serves an
important purpose in communicating to
the public that in most cases, impacts of
greater that 1⁄10 acre will be judged to be
more than minimal and will require
compensatory mitigation.
One commenter asked whether the
1⁄10 acre threshold for requiring
compensatory mitigation for wetland
losses also applies to non-wetland
waters of the United States. Several
commenters stated that compensatory
mitigation should be required for all
authorized impacts to waters of United
States. One commenter said that
compensatory mitigation for losses of
non-wetland waters of the United States
should be optional. Another commenter
said that on-site restoration of
temporarily impacted areas should be
achieved before compensatory
mitigation is required.
The 1⁄10 acre compensatory mitigation
threshold in paragraph (c) applies only
to wetland losses. We are adding a new
paragraph (d) to this general condition,
to clarify that the district engineer may
require compensatory mitigation for
losses of streams and other types of
waters of the United States. We do not
believe it is necessary to require
compensatory mitigation for all
authorized impacts to waters of the
United States. In response to preconstruction notifications,
compensatory mitigation requirements
for losses of streams and other open
waters will be determined by district
engineers on a case-by-case basis, to
ensure minimal adverse effects. The
NWP general conditions, especially
general condition 13, Removal of
Temporary Fills, address the restoration
of temporarily impacted areas.
Compensatory mitigation is required
only for permanent losses, however,
temporary impacts must also be
minimized.
Three commenters asked for specific
criteria that would be used by district
engineers to determine when
compensatory mitigation would be
required for NWP activities. Two
commenters requested clarification
regarding the circumstances when
compensatory mitigation would be
required for wetland losses of less than
1⁄10 acre. One commenter recommended
that permittees who believe their project
should not require compensatory
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mitigation be required to provide a
justification for why compensatory
mitigation is not necessary for their
NWP activities.
Compensatory mitigation
requirements will be determined by
district engineers on a case-by-case
basis, after considering relevant and
available information, such as the
ecological conditions of the project site,
the type of activity, the impacts of the
activity on the aquatic environment and
other public interest factors, and the
type of aquatic resources that will be
adversely affected by the NWP activity.
To the extent practicable, this
evaluation will be conducted using a
watershed approach. Compensatory
mitigation will be required for wetland
losses of less than 1⁄10 acre, when the
district engineer determines it is
necessary to ensure minimal adverse
effects on the aquatic environment. This
is particularly likely in areas where
there is concern for the cumulative
effects of multiple small losses. District
engineers will review pre-construction
notifications, and determine when
compensatory mitigation will be
required. It is not necessary to require
permittees to provide a statement
explaining why compensatory
mitigation is not needed, however
permittees are welcome to provide such
information if they believe it will help
the district engineer in determining the
amount and type of required mitigation.
Such statements are most useful when
they are based on sound technical
analysis using a watershed approach
that draws on pre-existing assessments
of watershed needs.
One commenter supported the
provision allowing the district engineer
to waive or reduce the compensatory
mitigation requirement for wetland
losses, when other forms of mitigation,
such as the establishment and
maintenance of riparian areas, would be
better for the environment. One
commenter said that off-site
compensatory mitigation should be
preferred in areas where invasive
species are a problem. One commenter
suggested that the general condition
retain a preference for restoration.
The location of compensatory
mitigation projects will be determined
on a case-by-case basis. Off-site
compensatory mitigation may be more
appropriate for a variety of reasons, in
addition to concerns for invasive
species. Off-site compensatory
mitigation may be more effective at
replacing aquatic resource functions
that will be lost as a result of the NWP
activity. Off-site mitigation may also
have a better chance of success,
particularly if the proximity of the
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permitted activity is likely to adversely
impact the mitigation (e.g., through
altered hydrology). This general
condition retains a preference for
wetland restoration, but the text has
been modified to reflect the language in
the 1990 ‘‘Memorandum of Agreement
Between the Environmental Protection
Agency and the Department of the Army
Concerning the Determination of
Mitigation Under the Clean Water Act
404(b)(1) Guidelines.’’
One commenter agreed with the oneto-one mitigation ratio in paragraph (c)
of this general condition, provided there
is flexibility in determining the
appropriate ratio for a specific NWP
activity. Several commenters said that
district engineers should be allowed to
require higher ratios of compensatory
mitigation, to help ensure effective
mitigation.
The mitigation ratio in paragraph (c)
is a recommended minimum ratio that
can be adjusted upward as necessary to
provide for more appropriate mitigation
for a specific activity. For a particular
NWP activity, the district engineer will
determine the appropriate mitigation
ratio. Ratios of greater than one-to-one
are often required to ensure that
appropriate amounts of compensatory
mitigation are provided to satisfy the
minimal adverse environmental effects
requirements of the NWPs. Higher ratios
may be used to address temporal losses,
uncertainty in mitigation success, and/
or differences in functions and services
between the impact site and the
mitigation site.
One commenter expressed support for
paragraph (d) of this general condition.
We are retaining this paragraph, with
slight changes to its text to provide
greater clarity. The substance of this
paragraph remains unchanged. Because
of the addition of a new paragraph (d),
this paragraph is redesignated as
paragraph (e).
Several commenters objected to
requiring riparian areas as
compensatory mitigation for activities
authorized by NWPs, stating that the
Corps lacks authority to require nonwetland riparian areas as compensatory
mitigation. One commenter provided
support for the use of riparian areas as
compensatory mitigation, and another
commenter said that riparian areas
should be required for all activities.
This commenter said that using riparian
areas as the only form of compensatory
mitigation is appropriate when the
project impacts would be more than
minimal without the protection of the
riparian area. Another commenter
asserted that the Corps is attempting to
expand its jurisdiction by requiring
establishment and maintenance of
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riparian areas. One commenter asked for
clarification of the jurisdictional status
of riparian areas under the Clean Water
Act. A commenter said that riparian
areas cannot be required as
compensatory mitigation for NWP
activities near streams because
compensatory mitigation projects may
only consist of areas that are, or will
become, waters of the United States.
The establishment and maintenance
of riparian areas can be required by the
district engineer as compensatory
mitigation, to help ensure that the NWP
activity results in minimal individual
and cumulative adverse effects on the
aquatic environment. Such a
requirement does not make non-wetland
riparian areas subject to Clean Water
Act jurisdiction. Since non-wetland
riparian areas are not jurisdictional, this
paragraph also states that legal
protection should be provided to the
riparian areas, for their protection and
maintenance. In many areas, riparian
areas will be wetlands subject to Clean
Water Act jurisdiction. In other areas
riparian areas will not meet the criteria
in the Corps wetland definition at 33
CFR 328.3(b).
We do not agree that the
establishment and maintenance of
riparian areas should be required for all
NWP activities. It may not be a
practicable or appropriate form of
compensatory mitigation for some NWP
activities.
Regardless of whether they are
wetland or non-wetland, riparian areas
generally provide ecological functions
that are important to the aquatic
environment, and especially to the
ecological integrity of streams.
Examples of ecological functions
provided by riparian areas include:
removing nutrients and pollutants from
surface runoff, which improves water
quality; moderating storm flows to
streams, which reduces downstream
flooding and degradation of aquatic
habitat; erosion reduction; moderating
water temperature changes; providing
detritus, a food source for many aquatic
organisms; providing a source of large
woody debris to stream channels, which
provides habitat for aquatic organisms;
providing habitat to a wide variety of
aquatic and terrestrial species; trapping
sediments, thereby reducing
degradation of stream habitat quality;
providing corridors for the movement
and dispersal of many species of
wildlife; and providing flood storage
capacity.
Compensatory mitigation projects can
include areas that are not waters of the
United States, as long as the mitigation
is directly related to the impacts of the
proposed work on such waters and
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appropriate to the scope and degree of
those impacts. Riparian areas are
integral components of streams and
other open waters, and are essential for
their ecological integrity and
functioning. The establishment and
maintenance of riparian areas as
compensatory mitigation for activities
authorized by NWPs and other types of
permits also helps advance the objective
of the Clean Water Act, which is to
‘‘restore and maintain the chemical,
physical, and biological integrity of the
Nation’s waters.’’ Therefore, riparian
areas can be required as compensatory
mitigation for NWP activities.
One commenter asked whether the
establishment and maintenance of
riparian areas as compensatory
mitigation is mandatory or
discretionary. Two commenters said
that in many areas with ephemeral
waters, it may not be possible to
establish and maintain riparian areas
next to those waters. Another
commenter stated that it is not always
feasible to provide legal protection (e.g.,
conservation easements) for riparian
areas within highway rights-of-way. One
commenter said that for ephemeral
streams, vegetated buffers should be
required instead of riparian areas.
The establishment and maintenance
of riparian areas as a compensatory
mitigation requirement is at the
discretion of the district engineer.
Compensatory mitigation requirements
are established on a case-by-case basis,
to ensure that the NWP activity results
in minimal individual and cumulative
adverse effects on the aquatic
environment. If ephemeral streams are
located on the project site, it may not be
feasible to establish and maintain
riparian areas next to those waters.
Riparian areas should be self-sustaining.
Also, if it is not possible to protect
riparian areas through real estate
instruments, the district engineer may
require alternate arrangements or an
alternative form of compensatory
mitigation, as appropriate to the
situation.
The general condition contains a
recommended width of 25 to 50 feet for
riparian areas on each side of the
stream. Two commenters said that
requiring 25 to 50 foot wide riparian
areas may not always be feasible, and
may be too costly. A commenter stated
that the recommended width of riparian
areas should be at least 150 feet to
protect water quality, and wider to
provide other ecological functions.
Another commenter suggested a
minimum width of 100 feet. One
commenter indicated that wider
riparian areas should be required to
address habitat issues identified in
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federal or state watershed plans.
Another commenter stated that wider
riparian areas should be required to
protect salmon habitat. One commenter
requested clarification regarding the
documentation necessary to determine
the appropriate width of the riparian
area.
The appropriate width of the riparian
area will be determined by the district
engineer, taking into account the
ecological characteristics of the project
site, as well as the nature and extent of
the overall activity that will be
constructed on the project site. The
recommended width for riparian areas
is intended to provide balance between
environmental protection and the
development of the project site. The
recommended width is also intended to
be commensurate with the level of
impacts that need to be mitigated. The
Corps’ regulations require compensatory
mitigation to be appropriate to the scope
and degree of the authorized impacts.
Requiring the establishment and
maintenance of a 150-or 100-foot wide
riparian area could comprise a
substantial land area on a parcel, and
would likely be an inappropriate
amount of compensatory mitigation for
an NWP activity, especially for an NWP
that has a 1⁄2 acre limit for losses of
waters of the United States. The
information provided in the site plans,
as well as supporting documentation, is
normally sufficient to determine the
appropriate width of the riparian area.
Another commenter said that there
needs to be flexibility to allow use of
other tools to protect water quality, such
as storm water management features,
instead of requiring the establishment
and maintenance of riparian areas. One
commenter stated that riparian areas
should be planted only with local
genetic stocks of native plant species.
Storm water management features, as
well as best management practices, may
be used instead of riparian areas to
protect water quality, if site
characteristics do not support the
establishment and maintenance of
riparian areas. Native species should be
planted, but we do not agree that it is
necessary to limit those plantings to
local genetic stocks, though this should
be encouraged where practicable. Such
stocks may not be available in the area,
and therefore such a requirement may
not be practicable.
Two commenters stated that this
general condition should clearly state
that mitigation banks can be used to
provide compensatory mitigation for
NWPs. One commenter said that the use
of mitigation banks to provide
compensatory mitigation for NWP
activities should be limited to the same
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watershed as authorized impacts. Two
commenters said that in-lieu fee
programs should not be used for the
NWPs. Another commenter stated that
in-lieu fee programs should not be used
for compensatory mitigation for NWP
activities unless they comply with 2000
in-lieu fee guidance. Two commenters
expressed support for the use of in-lieu
fee programs to provide compensatory
mitigation for NWP activities.
Both mitigation banks and in-lieu fee
programs can be used to provide
compensatory mitigation for activities
authorized by NWP permits. The
established service area of the
mitigation bank, as well as the judgment
of the district engineer, will be used to
determine whether credits provided by
that mitigation bank are appropriate
compensation for a specific NWP
activity. In-lieu fee programs can
provide compensatory mitigation
projects that benefit the aquatic
environment, as well as the watershed.
When the final Compensatory
Mitigation Rule is published, any
changes in mitigation requirements will
be applied to the NWP program as
necessary at that time.
Paragraph (g) of the proposed general
condition stated that compensatory
mitigation may be required to offset
permanent adverse effects to certain
functions and services provided by
waters of the United States, such as
converting a forested wetland to a
herbaceous wetland. Three commenters
objected to characterizing this as an
adverse effect. Two commenters said
that compensatory mitigation should
not be required for these impacts. Two
commenters asserted that this paragraph
should be deleted, since there is ample
guidance concerning when
compensatory mitigation should be
required for these types of impacts. Two
other commenters supported adding this
provision to the general condition.
We are retaining this provision, while
redesignating it as paragraph (h).
Compensatory mitigation can be
required for adverse effects to aquatic
resources, even specific functions
provided by those aquatic resources.
One commenter recommend adding
language to this general condition
which would state that the district
engineer will determine appropriate
compensatory mitigation based on what
is best for the aquatic environment on
a watershed basis. Another commenter
requested clarification that the
establishment of upland buffers around
compensatory mitigation projects is
voluntary, and compensatory mitigation
credit would be provided for such
vegetated buffers.
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We do not believe it is necessary to
revise the general condition to
specifically state that appropriate
compensatory mitigation will be
determined based on what would be
best for the aquatic environment on a
watershed basis, though this is certainly
the policy of the Corps. Mitigation
policy documents, such as Regulatory
Guidance Letter 02–02, already support
that concept. There is also an extensive
discussion of the watershed approach in
the preamble to the proposed
Compensatory Mitigation Rule. District
engineers may grant compensatory
mitigation credit for upland buffers
surrounding compensatory mitigation
project sites, if those buffers contribute
to the ecological functioning and
sustainability of those projects. Any
requirement to establish and maintain
vegetated buffers around compensatory
mitigation project sites should be based
on considerations of practicability and
appropriateness.
One commenter asserted that the
Corps does not have the statutory
authority to require conservation
easements to protect compensatory
mitigation projects. This commenter
said that such a requirement is
problematic for mining activities
because different parties may own
different rights (e.g., surface rights v.
mineral rights) associated with the
parcel of land.
The district engineer has the
discretion to require conservation
easements for compensatory mitigation
project sites, to protect those sites, if he
or she determines that this is necessary
to ensure minimal adverse impacts. In
some cases, it may not be feasible to
require conservation easements because
the various rights associated with a
particular parcel of land may belong to
different individuals. In such cases,
other methods of protecting the
mitigation site should be explored.
One commenter said that this general
condition should be revised to provide
performance standards for
compensatory mitigation projects
required for NWP activities. This
commenter also recommended retaining
the requirement for NWP verifications
to specify the party responsible for
implementing the compensatory
mitigation plan, instead of limiting it
only to cases where the use of
mitigation banks, in-lieu fee programs,
and activity-specific compensatory
mitigation is required.
Performance standards for
compensatory mitigation projects are
usually specific to certain types of
aquatic resources and are, therefore,
more appropriately determined by the
district engineer. It would be
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inappropriate to establish national
performance standards through this
general condition, because of the
considerable variation among aquatic
resource types across the country.
Paragraph (g) of this general condition
requires the mitigation provisions of
NWP verifications to specify the party
responsible for providing compensatory
mitigation. This requirement applies to
all three types of compensatory
mitigation, including compensatory
mitigation provided by the permittee.
General condition 20 is adopted, with
the modifications discussed above.
GC 21. Water Quality. We proposed to
modify this general condition by
simplifying the provision regarding
requirements for water quality
management measures.
Several commenters expressed
support for the proposed changes to this
general condition. One commenter
suggested that this general condition
should not apply to NWPs 27 or 48,
because the activities authorized by
these NWP result in improvements to
water quality.
If an aquatic habitat restoration,
establishment, or enhancement activity
or a commercial shellfish aquaculture
activity involves discharges of dredged
or fill material that require a section 404
permit, then water quality certification
must be obtained, either for the NWP
generally or individually by the project
proponent, or waived. This is a
requirement of Section 401 of the Clean
Water Act. Therefore, we cannot modify
this general condition to exclude NWPs
27 or 48.
Several commenters stated that this
general condition creates the potential
for duplicative oversight of water
quality issues by the Corps and EPA or
its designated state agency. Another
commenter said that it would be
arbitrary for the Corps to attempt to
regulate water quality by requiring some
type of undefined water quality
management measures.
Whether duplicative or not, Section
401 certification by EPA or a State or
Tribe, as appropriate, is required by the
Clean Water Act. District engineers can
condition NWP authorizations to ensure
that the authorized activity results in
minimal individual and cumulative
adverse effects on the aquatic
environment and other factors of the
public interest, including water quality.
By requiring water quality management
measures necessary to ensure that the
authorized activity results in minimal
adverse effects, the Corps is not
attempting to regulate water quality.
Appropriate water quality management
measures will be identified on a case-
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by-case basis through the NWP
verification process.
A Section 401 certification must be
obtained or waived prior to
commencing the authorized activity. In
cases where a state has not yet provided,
or has denied, water quality
certification, for an NWP generally, the
permittee must request individual
certification before proceeding and
provide documentation of this request
to the Corps. The district engineer will
wait for a reasonable period of time after
receipt of this documentation. The NWP
regulations generally define this period
of time as 60 days, after which the
district engineer can assume a waiver of
the water quality certification. The wait
period may vary as a result of
negotiations between the district
engineer and the state, but it cannot
exceed one year. The district engineer
will inform the project sponsor of the
appropriate waiting period for
presumption of a waiver of certification.
The activity may not proceed until the
project sponsor has received individual
certification from the state or the
waiting period has elapsed. This general
condition is adopted as proposed.
GC 22. Coastal Zone Management. We
proposed to modify this general
condition to state that the district
engineer or state may require additional
measures to ensure consistency with
state coastal zone management
requirements.
One commenter stated that use of the
term ‘‘waived’’ in this general condition
is inappropriate, because Coastal Zone
Management Act (CZMA) consistency
determinations cannot be waived. This
commenter also stated that obtaining a
CZMA consistency concurrence cannot
be a condition of a Federal permit,
because the CZMA states that a Federal
permit cannot be issued until a CZMA
consistency concurrence is issued.
We have modified this general
condition by removing the phrase ‘‘or
waived’’ and replacing it with the
phrase ‘‘or a presumption of
concurrence must occur’’ to be
consistent with the implementing
regulations for the CZMA. This general
condition is an appropriate means of
ensuring compliance with CZMA
requirements, especially for those NWP
activities that do not require preconstruction notification. For activities
subject to the CZMA, the NWP
authorization is not valid until the
permittee has complied with the
requirements of the CZMA, including
the requirement to obtain CZMA
consistency concurrence or a
presumption of concurrence.
A CZMA concurrence or presumption
of concurrence must be obtained prior
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to commencing the authorized activity.
In cases where a state has not acted on,
or has disagreed with the Corps’
consistency determination, the
permittee must provide the state with an
individual consistency determination
for concurrence, and must provide the
district engineer with the state’s
individual consistency concurrence or a
copy of the individual consistency
determination provided to the state for
concurrence. If the state fails to act on
the permittee’s consistency
determination within six months of
receipt by the state, concurrence will be
presumed.
This general condition is adopted
with the modification discussed above.
GC 23. Regional and Case-by-Case
Conditions. We proposed to modify this
general condition to clarify that water
quality certifications may be issued by
Indian Tribes or the U.S. Environmental
Protection Agency, and that states issue
CZMA consistency determinations.
One commenter recommended
modifying this general condition to
clarify that the U.S. EPA has delegated
the section 401 water quality
certification program to many states,
and that in those cases it is the
designated state that issues the water
quality certification, not the U.S. EPA.
We do not agree that this suggested
modification is necessary, since the
wording already recognizes that
delegated States or Tribes may issue
Section 401 water quality certifications.
This general condition is adopted as
proposed.
GC 24. Use of Multiple Nationwide
Permits. We proposed to modify this
general condition by making a
grammatical adjustment.
Several commenters objected to the
practice of using more than one NWP to
authorize a single and complete project.
In contrast, two commenters said that
combining NWPs is both appropriate
and desirable as a means for the Corps
to reduce its workload and provide
expedited approvals to the regulated
public. Two comments said that the
proposed general condition has the
effect of raising the acreage limit when
an NWP with an acreage limit is
combined with another NWP that has
no set limit. One commenter suggested
rewording the general condition in the
affirmative. One commenter suggested
replacing the term ‘‘temporary loss’’
with ‘‘temporary impact’’ for purposes
of calculating the loss of waters of the
United States.
We agree that the ability to use
multiple NWPs reduces our workload
and expedites decisions for the
regulated public while maintaining the
necessary protections for the aquatic
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environment. When two NWPs are used
to authorize a single and complete
project, and one NWP has a specified
limit and the other NWP has no
specified limit, the general condition
states that the acreage loss of waters of
the United States cannot exceed the
acreage limit of the NWP with the
highest specified acreage limit. The
NWP with the specified acreage limit
establishes the acreage limit for the
single and complete project, not the
NWP with no designated acreage limit.
We believe phrasing this general
condition as a prohibition assists in
compliance. The reference to ‘‘acreage
loss’’ in this general condition applies to
permanent losses, to be consistent with
the definition of ‘‘loss of waters of the
United States’’ provided in the
‘‘Definitions’’ section of the NWPs.
This general condition is adopted as
proposed.
GC 25. Transfer of Nationwide Permit
Verifications. We proposed to add this
new general condition to the NWPs.
Several commenters supported the
proposed general condition. One
commenter requested clarification
whether there would be a standardized
form for the parties to sign and submit.
Another commenter recommended
adding a permit transfer form as a
separate section of the NWP verification
or certificate of compliance.
This general condition provides
specific language that must be included
in all NWP verification transfer request
letters from the original permittee to the
appropriate Corps district office, to
validate the transfer of the NWP
verification to a new property owner.
District engineers have the discretion to
incorporate this language in NWP
verification letters, either as language
within the text of the letter, or as a
separate form or attachment. At their
discretion, district engineers may also
ask permittees to include the referenced
language as part of their own transfer
request letter.
One commenter requested
clarification whether the permit transfer
information would be tracked in a
database and made available to the
public and other regulatory agencies.
The permit transfer authorization
information will be retained in the
appropriate recordkeeping facilities at
Corps district or field offices. The
information will be provided upon
request to the public or other agencies.
One commenter recommended adding
a sentence to the transfer statement to be
signed, specifying that any changes in
the permitted project must be evaluated
by the district engineer and could
require modifications to the permit.
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Any requests for modification of an
activity previously authorized by a DA
permit will be reviewed by the district
engineer. If the new proponent wants to
modify the previously verified activity,
the proposed modification must be
submitted for the consideration of the
Corps, to verify that the activity still
complies with the terms and conditions
of the applicable NWP. We do not
believe it is necessary to add a sentence
to this general condition to describe this
requirement, which applies regardless
of whether the permit is transferred or
not.
Several commenters stated that this
general condition only addresses the
sale of the property associated with an
NWP verification, and recommended
that it be expanded to allow the transfer
of a permit verification when
responsibility over the project is
transferred even if the lands in question
do not undergo change in ownership.
Another commenter suggested clarifying
that the transfer provision is also
applicable when only part of the
property covered by the NWP is sold.
This commenter also suggested
changing the phrase ‘‘associated
liabilities associated with compliance
with its terms and conditions’’ to read
‘‘obligations to comply with its terms
and conditions.’’
The language for the proposed general
condition was taken from Appendix A
of 33 CFR 325, which is the standard
form for Department of the Army
permits. This language is found at
general condition 4 of Appendix A. We
believe that the language in this general
condition should be consistent with our
standard permit language.
One commenter requested
clarification on how the NWP
verification transfer would affect off-site
mitigation requirements associated with
an NWP verification. One commenter
requested clarification as to whether the
transfer is a required condition or an
option.
As stated in this general condition,
when a property associated with an
NWP verification is sold, the
responsibilities and liabilities associated
with the NWP verification are
transferred to the new owner. This
includes any mitigation requirements
added as special conditions to the NWP
authorization being transferred.
Transferring the NWP verification to the
new owner of the property is not
necessary if the new owner decides not
to conduct the authorized activity. The
new owner also has the option of
obtaining a different NWP verification.
However, if the activity is (or was)
conducted and any permit conditions
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are still applicable, the new owner must
have some form of DA authorization.
This general condition is adopted as
proposed.
GC 26. Compliance Certification. We
did not propose any substantive changes
to this general condition. One
commenter suggested changing the
name of this general condition to
‘‘Compliance Verification’’ to avoid
confusion with other certifications such
as water quality certifications.
We do not agree with the proposed
name change for this condition. For this
general condition, the permittee is
certifying that he or she has completed
the authorized work and any required
mitigation.
This general condition is adopted as
proposed.
GC 27. Pre-Construction Notification.
We proposed to modify and simplify
this general condition by removing
language that is redundant with the
terms of specific NWPs. We also
proposed to modify the information
requirements for pre-construction
notifications. Other proposed
modifications are discussed in the
September 26, 2006, Federal Register
notice.
Two commenters stated that the
reference to using ENG FORM 4345
should be removed because this form
does not contain the necessary
information required for a complete preconstruction notification. One
commenter requested that a complete
pre-construction notification be defined.
It is not necessary to use ENG FORM
4345 for pre-construction notifications.
Instead of using ENG FORM 4345, a
prospective permittees may choose to
supply the information in a letter. Some
districts provide checklists to assist
prospective permittees, especially if
they have regional conditions that
specify additional information that must
be submitted with pre-construction
notifications.
One commenter asked if a preconstruction notification is presumed to
be complete if the district engineer does
not request additional information
necessary to make the pre-construction
notification complete within 30 days.
This commenter also requested
clarification on when the 45-day preconstruction notification review period
begins. One commenter suggested that
the district engineer should be allowed
to make more than one request of
additional information in order to make
a more informed decision.
If 30 days has passed since the preconstruction notification was received
by the Corps district, the preconstruction notification will be
presumed to be complete. The 45 day
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pre-construction notification review
period begins on the date the complete
pre-construction notification is received
by the Corps district. If the district
engineer requests additional
information necessary to make the preconstruction notification complete, a
new 45 day review period begins on the
date the requested information is
received by the Corps district. If no
request for additional information is
received, the original pre-construction
notification is deemed complete and the
45 day review period begins on the date
the pre-construction notification was
received by the Corps district.
The provision limiting the district
engineer to one request for additional
information applies only to those
requests for information necessary to
complete the pre-construction
notification. We have modified the
second sentence of paragraph (a) to
provide flexibility in cases where there
are extenuating circumstances that
warrant an additional request for
information necessary to make a preconstruction notification complete.
Such requests must also be made within
the 30 calendar days of receipt of the
pre-construction notification. This
sentence has been modified to state that,
as a general rule, the district engineer
will make only one request for
additional information to make the preconstruction notification complete.
District engineers should endeavor to
make only one request for additional
information to make a pre-construction
notification complete.
The information requirements for a
complete pre-construction notification
are provided in paragraph (b) of this
general condition. We believe the
information required for a complete preconstruction notification is the
minimum information necessary for
district engineers to begin the process of
determining whether the proposed work
will result in minimal adverse effects on
the aquatic environment and is
authorized by NWP.
If, as a result of the review of the
complete pre-construction notification,
the district engineer determines that
additional information (such as a
compensatory mitigation plan) is
needed to make a final decision on
whether the activity qualifies for NWP
authorization or discretionary authority
should be asserted, the district engineer
may request that information. In cases
where this additional information is
necessary to make a decision on the preconstruction notification, the decision
must still be made within 45 days of the
receipt date for the complete preconstruction notification.
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Two commenters said that the burden
has shifted from the Corps to the
prospective permittee for Endangered
Species Act or National Historic
Preservation Act compliance, and there
is no relief provided in the 45 day clock
for applicants when Endangered Species
Act or section 106 consultation is
necessary. Two commenters stated that
if the 45 day period has passed, the
NWP verification should be issued even
if the Endangered Species Act or section
106 requirements have not been
completed. One commenter inquired if
the Corps could ensure that the
Endangered Species Act or National
Historic Preservation Act consultation
processes will conclude within 45 days.
One commenter said that paragraphs
(b)(6) and (b)(7) of this general condition
should clarify whether Federal
permittees are required to submit
information for compliance with the
Endangered Species Act or Section 106
of the National Historic Preservation
Act.
Permittees cannot presume NWP
authorization if any endangered or
threatened species or critical habitat
might be affected or is in the vicinity of
the project or if the project is located in
designated critical habitat, or if the
activity may have the potential to cause
effects to any historic properties listed,
determined to be eligible for listing, or
potentially eligible for listing on the
National Register of Historic Places (see
general conditions 17 and 18). The NWP
regulations state that if the prospective
permittee notifies the district engineer
that Federally-listed endangered or
threatened species or critical habitat
might be affected or are in the vicinity
of the project, he or she cannot begin
work until notified by the district
engineer that the requirements of the
Endangered Species Act have been
satisfied (see 33 CFR 330.4(f)(2)). There
is a similar provision for historic
properties (see 33 CFR 330.4(g)(2)). We
have modified general conditions 17
and 18 to require district engineers to
inform permittees of the need to
conduct these consultations within 45
days of receipt of complete preconstruction notifications, however,
even if such notice is not received, the
permittee cannot assume authorization.
The permittee makes the first
determination as to whether general
conditions 17 or 18 are triggered, and
will know if he or she has notified the
Corps of any potential effects on listed
species or critical habitat, or on historic
properties. If so, the permittee must wait
for written verification from the Corps
that ESA and historic preservation
requirements have been satisfied. In
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cases where Endangered Species Act or
section 106 consultation is necessary,
we cannot require those consultations to
be concluded with 45 days of receipt of
a complete pre-construction
notification. Those consultations often
take more than 45 days; their
timeframes are only partially within the
control of the Corps. The Corps will do
what it can to expedite any required
consultations.
We have inserted the phrase ‘‘for nonFederal permit applicants’’ in
paragraphs (b)(6) and (b)(7) since
Federal permittees are to follow their
own procedures for complying with the
Endangered Species Act and the
National Historic Preservation Act. Nonfederal permittees are required to
submit the information required by
these paragraphs, since the Corps will
use that information to determine
whether it is necessary to conduct
Section 7 or Section 106 consultations
for those activities that may affect listed
species, critical habitat, or historic
properties.
One commenter recommended
modifying paragraph (b) of this general
condition to include guidance on the
types of information and analyses that
should be submitted with preconstruction notifications to support
‘‘effect’’ determinations and
consultation efforts under Section 7 of
the Endangered Species Act. This
commenter said that this guidance
should include instructions on how
prospective permittees can obtain
species lists. This commenter also
suggested amending paragraph (b) to
include guidance on evaluating ‘‘effects
of the action’’ and constructing
‘‘consultation packages’’ for informal
and formal Section 7 consultation.
In paragraph (e) of general condition
17, Endangered Species, we have
provided the links to the Web sites of
the U.S. Fish and Wildlife Service and
the National Marine Fisheries Service,
where prospective permittees can go to
obtain further information on
endangered or threatened species or
critical habitat. The available
information regarding endangered or
threatened species or critical habitat
varies by Service field office, and we
believe providing a general link is
sufficient since their Web pages are
likely to change over time. As for
providing guidance regarding
information and analyses to be used for
Endangered Species Act compliance, it
would be more appropriate for our
district offices to work with the field
offices of the Services to develop such
guidance as necessary, since the
appropriate types of information and
analyses are likely to vary by species,
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and the type of activity being
conducted.
One commenter stated that assuming
the NWP verification after 45 days is
problematic because many states require
the Corps verification letter prior to
commencing the water quality
certification review.
In cases where the 45 day preconstruction review period has passed,
the permittee must still comply with
general condition 21, Water Quality.
After the applicant has submitted an
application for individual water quality
certification, waiver of the requirement
to obtain water quality certification for
an NWP is assumed if the applicant has
not heard from the state or Tribe within
a reasonable amount of time, generally
60 days (see 33 CFR 330.4(c)(6)). If the
state requires a Corps verification for
water quality certification, the permittee
must wait for the verification. The Corps
will make every effort to provide
verification letters within 45 days.
One commenter said that the 45 day
default authorization provision should
be eliminated and two commenters
requested that the 45 day review period
be reduced to 30 days. Two commenters
asked if the time frames are measured in
calendar days or business days. One
commenter requested a list of potential
differences in information requirements
for pre-construction notifications for the
various NWPs.
We are maintaining the 45 day default
authorization provision. We are
modifying the text of general condition
27 to clarify that calendar days are used.
Paragraph (b) of this general condition
lists all of the information necessary for
a complete pre-construction
notification. Corps districts can provide
checklists to assist prospective
permittees, especially if they have
regional conditions that specify
additional information that must be
submitted with pre-construction
notifications.
Two commenters expressed support
for removing part of (a)(2) from the
notification general condition adopted
in 2002. One commenter suggested
modifying paragraph (a)(2) to state that
a prospective permittee cannot begin an
NWP activity that requires a written
waiver of NWP limits, until the written
waiver is issued by the district engineer.
One commenter said the district
engineer should be required to provide
written waivers to prospective
permittees within the 45 day timeframe.
We have modified paragraph (a)(2) to
state that the permittee cannot begin the
activity until the district engineer issues
the written waiver required by an NWP.
Such waivers do not have to be
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provided during the 45-day preconstruction notification review period,
because the written waiver is required
by the terms and conditions of the
applicable NWP. For proposed projects
that require any type of written waiver,
district engineers must make a written
determination that the proposed work
will result in no more than minimal
adverse effects on the aquatic
environment. District engineers will try
to determine whether or not to grant
waivers as expeditiously as possible.
One commenter expressed support for
the proposed changes to paragraph
(b)(3). Another commenter said that
paragraph (b)(3) contains an incomplete
sentence. One commenter
recommended adding a requirement for
the prospective permittee to state how
avoidance and minimization was
accomplished in order for the Corps to
make a better decision. One commenter
suggested that the prospective permittee
should list any waivers that are
requested. One commenter said that
paragraph (b)(3) should be modified to
require analyses of losses of juvenile
salmonid over wintering habitat and
early rearing habitat.
We have inserted the words ‘‘and to
determine the need for’’ before ‘‘any
necessary compensatory mitigation’’ to
complete the sentence in paragraph
(b)(3). District engineers will review preconstruction notifications in accordance
with general condition 20, Mitigation, to
determine whether the prospective
permittee has accomplished all
practicable avoidance and minimization
on the project site. The present
information requirements in paragraph
(b)(3) will suffice for determining
whether waivers of NWP limits are
being requested by the prospective
permittee. Assessments of potential
impacts to juvenile salmon are more
appropriately addressed by Corps
districts where significant salmon
impacts are occurring.
Two commenters agreed with the
requirement to include a delineation of
wetlands and other waters of the United
States with the pre-construction
notification. One commenter asked if an
approved jurisdictional determination is
necessary for a complete preconstruction notification. One
commenter said that the general
condition should clarify whether a
prospective permittee can assume that a
delineation submitted with a preconstruction notification is an approved
jurisdictional determination. One
commenter stated a delineation of
special aquatic sites should be required
for NWPs 3, 11, 13, 19, 27, 29, 31 and
36. Two commenters voiced concern
that delineating wetlands and waters of
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the United States beyond those actually
impacted by the project is too
burdensome when working on large
project sites.
The permittee cannot assume that a
delineation of waters of the United
States submitted with a pre-construction
notification is an approved
jurisdictional determination.
Jurisdictional determinations are made
by the Corps and documented through
the issuance of an NWP verification.
The Corps is in the process of revising
its procedures for issuing and
documenting its jurisdictional
determinations, and will be providing
guidance shortly.
The 45-day pre-construction
notification review period starts on the
date that a complete pre-construction
notification is received. If the district
engineer determines that the delineation
is incorrect and requests a revised
delineation from the applicant, the 45day review period starts again when the
revised delineation is received by the
district engineer. This general condition
requires delineations of special aquatic
sites and other waters of the United
States on the project site, so it is not
necessary to specify which NWPs
require delineations with their preconstruction notifications. Since this
paragraph refers to project site, it does
not imply that all waters of the United
States on the property need to be
delineated. The delineation need only
cover a sufficient area surrounding the
proposed NWP activity.
One commenter stated the while the
methodology for delineating wetlands is
established, methods for delineating
non-wetland waters of the United States
are lacking. One commenter voiced
concern with the language stating that
the delineation must be prepared in
accordance with the ‘‘current method
required by the Corps’’ and requested
that we state that wetland delineations
cannot be based solely on National
Wetland Inventory maps because they
were not developed for the 404 program.
Furthermore, it was urged that the Corps
require field-based delineations and not
approve any delineations for waters of
the United States, including wetlands,
without a field inspection.
Delineations of non-wetland waters of
the United States should follow the
definitions for these areas. For example,
in using the definition for riffle and pool
complexes, maps indicating stream
segments containing riffle and pool
complexes and their location can be
used as delineations of these special
aquatic sites. It is not necessary to
precisely map each riffle and pool
complex within a stream. Rather, the
delineation need only show the
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locations of special aquatic sites at a
sufficient level of detail for the district
engineer to determine the potential for
these sites to be impacted by project
activities.
The reference to the ‘‘current method’’
means the 1987 Corps of Engineers
Wetland Delineation Manual, associated
guidance, and any approved regional
supplements to the 1987 manual.
National Wetland Inventory maps are
useful for planning purposes but they
do not provide delineations of waters of
the United States. It is not necessary to
require field inspections for all
delineations of waters of the United
States.
One commenter expressed concern
regarding the language in paragraph
(b)(4) that discusses situations where
the Corps would conduct delineations.
In this paragraph we are simply stating
that if a prospective permittee relies on
the Corps to conduct a delineation, that
prospective permittee should anticipate
delays due to the workloads facing the
district engineers.
One commenter suggested modifying
paragraphs (b)(5) and (e) to clarify that
these paragraphs refer to permanent
losses. One commenter recommended
changing paragraph (b)(5) to require the
prospective permittee to state why the
project would exceed minimal adverse
impacts without additional mitigation.
Two commenters suggested that there
should not be a requirement to submit
detailed compensatory mitigation plans
with a pre-construction notification,
because of the costs to develop
mitigation plans that may not be
required once the district engineer
makes a decision on the preconstruction notification.
It is unnecessary to modify these
paragraphs to specify that we are
referring to permanent losses, because
the NWP definition for ‘‘loss of waters
of the United States’’ refers only to
permanent losses. In fulfilling the
requirements of paragraph (b)(5), the
prospective permittee’s statement can
explain how the proposed activity
complies with general condition 20.
Paragraph (c) of general condition 20
states that the district engineer can
waive the requirement for wetlands
compensatory mitigation or require an
alternate form of mitigation. We are
modifying paragraph (b)(5) of this
general condition to allow project
proponents to submit conceptual or
detailed mitigation plans.
One commenter said that a conceptual
mitigation plan is not sufficient and
detailed plans should be required. One
commenter requested that detailed
compensatory mitigation monitoring
plans be required for activities
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authorized by NWPs 12, 14, 21, 29, 39,
40, 41, 42, 43, 44, 45, 46, 47, 48, 49, and
50.
Conceptual mitigation plans are
appropriate for submittal with preconstruction notifications. These
conceptual plans are useful in making
initial determinations regarding the
appropriateness of proposed
compensatory mitigation. If not
submitted with the pre-construction
notification, detailed compensatory
mitigation plans will be required prior
to commencing the authorized activity
in cases where the permittee is
performing the mitigation. If the
permittee is using a mitigation bank or
in-lieu fee program, he or she must
provide the name of the bank or
program and the number and type of
credits being purchased.
One commenter suggested that
paragraph (d)(2) be modified to include
NWPs 20 and 38 with NWP 37, because
of the emergency nature of these
activities. We do not agree that this is
necessary, because NWP 20 does not
require pre-construction notification
and NWP 38 is not limited to emergency
situations. We are adding numbers to
the paragraphs within paragraph (d) to
provide greater clarity.
One commenter recommended
modifying paragraph (d) to reduce the
acreage threshold for agency
coordination from 1⁄2 acre to 1⁄10 acre,
because of the 1⁄10 acre threshold for
wetlands compensatory mitigation.
The present threshold for agency
coordination is sufficient, since
activities resulting in the loss of greater
than 1⁄2 acre of waters of the United
States have greater potential to result in
more than minimal adverse effects.
Decisions regarding the amount and
type of compensatory mitigation that
should be required for NWP activities
are made by district engineers on a caseby-case basis in accordance with general
condition 20 and other appropriate
regulations and guidance. Requiring
agency coordination for losses of less
than 1⁄2 acre would result in a
substantial workload increase to Corps
districts and the resource agencies, and
is unlikely to provide significant
additional protection for the aquatic
environment.
One commenter said that the
authority to sign NWP verifications
should not be delegated to Corps project
managers.
Districts have the authority to
determine the appropriate level of
signature authority for NWP
verifications, to implement the NWP
program effectively.
This general condition is adopted
with the modifications discussed above.
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GC 28. Single and Complete Project.
We are adding a new general condition
to clarify that the NWPs authorize only
single and complete projects. This is in
response to a commenter’s concern
about the removal of language from the
2002 NWPs which limited the use of
certain NWPs to a single and complete
project or a part of a single and
complete project. That language was in
NWPs 13, 15, 18, 19, 29, 39, 42, 43, and
44.
Limiting all NWPs to authorize only
single and complete projects is a longstanding practice. In this new general
condition, the authorized activity must
be a single and complete project. In
addition, this general condition states
that the same NWP can be used only
once to authorize that single and
complete project. For example, NWP 39
cannot be used twice to authorize a
commercial development. This general
condition is consistent with general
condition 24, Use of Multiple
Nationwide Permits. The new general
condition will help improve
environmental protection by clarifying
that piecemealing of activities that
require Department of the Army permits
is prohibited.
Former general condition 27.
Construction Period. We proposed to
remove this NWP general condition.
Several commenters expressed
support for the removal of this general
condition, stating that it would
eliminate confusion about the time
frames when the NWPs are in effect.
Several commenters objected to the
elimination of this general condition,
stating that it was needed since it took
into account unexpected situations,
which can delay the completion of a
project. One commenter opposed the
removal of this general condition,
stating that it provided necessary
flexibility at the end of a NWP cycle,
and still allowed the permittee to
complete the work without having to
request another permit or verification
from the Corps. Several other
commenters said that elimination of this
general condition could result in
considerable delays and economic
burdens for completion of projects with
no more than minimal adverse effects.
One commenter stated that removing
this general condition would result in
more individual permits for activities
that would not result in more than
minimal impacts.
We are removing this general
condition, because it does not comply
with Section 404(e)(2) of the Clean
Water Act, which places a five-year
limit on general permits issued under
section 404. Since this general condition
did not specify any limits on project
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completion dates, in effect it provided
the district engineer with the authority
to state that the NWP activity was
authorized for any period of time. We
believe that this is contrary to section
404(e)(2).
Under the current NWP regulations,
district engineers may issue NWP
verification letters that are valid for a
period of two years. In cases where an
NWP verification letter expires before
the NWP itself expires, the activity
continues to be authorized by the NWP
until the NWP expires. It is not
necessary to issue a new verification
during the five year period the NWP is
in effect. Any special conditions that
were imposed by the district engineer
remain in effect after the NWP
verification expires, unless the district
engineer removes those conditions.
Once the NWP expires, the permittee
can utilize 33 CFR 330.6(b) to complete
the work. That regulation allows
permittees to continue work for one year
in reliance on an NWP authorization, if
that NWP has expired or been modified
or revoked, and the activity is under
construction or under contract to
commence construction. If that work
cannot be completed within that oneyear time period, then the permittee
would have to obtain another DA
authorization. We continue to believe
that 33 CFR 330.6(b) is sufficient to
address the concern with projects that
may not be completed before an NWP
expires. For NWP activities that will
require substantial amounts of time to
complete, project proponents should
consider whether it would be more
advantageous to pursue an individual
permit authorization. Individual permits
can authorize greater flexibility in
construction periods. An individual
permit authorization can also be
extended, as long as the district
engineer determines that the time
extension would be consistent with
applicable regulations and would not be
contrary to the public interest.
One commenter requested
clarification on whether newly issued
NWP verifications for specific projects
would be valid for five years or for only
one to two years. Two commenters
suggested that all NWP verifications
should be issued with five-year
expiration periods. Another commenter
suggested that all NWP verifications
should be set to expire concurrently
with the NWPs themselves. Similarly,
another commenter requested
clarification on whether applicants
could request NWP verifications with
expiration dates corresponding to the
new NWPs expiration date.
In the November 30, 2004, issue of the
Federal Register (69 FR 69567) we
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published a proposed rule that would
allow district engineers to issue NWP
verifications that would expire on the
same date the NWP expires. Until that
final rule is issued, the current 33 CFR
330.6(a)(3)(ii) applies, which states that
an NWP verification letter can be valid
for no more than two years. However, as
stated above the activity continues to be
authorized by the NWP until the NWP
expires.
Definitions
One commenter said that the NWP
definitions should be promulgated
through the Administrative Procedure
Act rulemaking process, and placed in
the Code of Federal Regulations since
many of these terms apply to other
aspects of the regulatory program.
The definitions adopted today have
been promulgated through the
Administrative Procedure Act process.
These definitions apply only to the
NWP program. A separate rulemaking
action would be required to adopt
definitions with general applicability to
the Corps Regulatory Program.
One commenter asked for definitions
of ordinary high water mark, adverse,
land, waters of the United States,
environmental, environmental impact,
‘‘a timely manner’’, regulatory
efficiency, cumulative impacts, public
interest factors, mitigation banks,
permittee-responsible mitigation, in-lieu
fee program, aquatic resource functions,
and grandfathering. Another commenter
requested a definition of ‘‘temporary
loss.’’
We are providing a separate definition
of ordinary high water mark. Previously,
this definition was in the definitions of
‘‘open water’’ and ‘‘waterbody.’’ The
term ‘‘waters of the United States’’ is
defined at 33 CFR part 328. We do not
believe it is necessary to define, for the
purposes of the NWP program, the terms
‘‘environmental,’’ ‘‘environmental
impact,’’ ‘‘a timely manner,’’ ‘‘regulatory
efficiency,’’ or ‘‘grandfathering.’’
Commonly accepted definitions for
those terms are sufficient for the
implementation of the NWP program.
The Corps uses the definition of the
term ‘‘cumulative impact’’ from the
Council on Environmental Quality’s
regulation at 40 CFR 1508.7. The terms
‘‘mitigation bank’’ and ‘‘in-lieu fee
program’’ are currently defined by the
November 28, 1995, mitigation banking
guidance (60 FR 58605). The
grandfather provisions for NWP
authorizations are provided at 33 CFR
330.6(b). It is more appropriate to define
the terms ‘‘permittee-responsible
mitigation’’ and ‘‘aquatic resource
functions’’ through the promulgation of
the final compensatory mitigation rule
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required by Section 314 of the National
Defense Authorization Act for Fiscal
Year 2004. Defining ‘‘temporary loss’’ is
not desirable, because it would likely
result in a reduction in flexibility in
implementation of the NWP program.
Where there is ambiguity, district
engineers should have flexibility to
determine, on a case-by-case basis,
whether a particular activity causes a
temporary or permanent loss of waters
of the United States.
Two commenters requested a
definition of ‘‘minimal effects.’’ Another
commenter said that this term should be
defined regionally, since it cannot be
defined at a national level.
We continue to maintain our position
that the term ‘‘minimal effects’’ cannot
be simply defined at a national level. It
is challenging to define it precisely even
at smaller scales, such as states or
watersheds. There is considerable
variation in aquatic resource functions,
services, and values across the country.
There is also wide variation in those
functions, services, and values at
smaller landscape scales. Site-specific
factors, such as the types and amounts
of functions provided by waters, the
services those aquatic resource
functions provide, the value society
places on those functions and services,
the geomorphic setting of those waters,
and other factors are important to
consider when determining whether an
NWP activity will result in minimal
adverse effects on the aquatic
environment. We believe the term
‘‘minimal,’’ while not precise, is well
understood by the public and has not
caused undue confusion in the
implementation of the Section 404
program to date. A certain amount of
flexibility on the part of district
engineers to determine what is
‘‘minimal’’ in a particular context, after
consideration of the factors discussed
above, is necessary for the practical
implementation of the program.
Best management practices (BMPs).
We proposed to modify this definition
by removing the last sentence. One
commenter suggested that we
acknowledge that BMPs may have
impacts on groundwater and subsurface
water.
Although best management practices
may impact hydrology, the definition
need not address that issue. The
definition is adopted as proposed.
Compensatory mitigation. We
proposed to modify this definition by
removing the phrase ‘‘For the purpose of
Section 10/404, compensatory
mitigation is.’’ We also proposed to
replace ‘‘creation’’ with establishment
(creation).’’ One commenter expressed
support for removing ‘‘exceptional
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circumstances’’ in relation to the use of
preservation as a type of compensatory
mitigation. One commenter stated that
‘‘aquatic resource’’ should be defined in
the context of jurisdiction. Another
commenter stated that this definition
should be consistent with the other
terms for different types of
compensatory mitigation that are
provided in this section, specifically the
definition provided for establishment
(creation).
Compensatory mitigation may be
provided by aquatic resources that are
not subject to the Corps regulatory
jurisdiction. Therefore, it is not
necessary to modify this definition by
replacing ‘‘aquatic resources’’ with
‘‘waters of the United States.’’ We have
added the word ‘‘creation’’, to be
consistent with ‘‘establishment
(creation),’’ which is defined in this
section. The definition is adopted as
proposed.
Currently serviceable. We proposed to
move the term and definition from NWP
3 to this section since it is used for other
NWPs. One commenter suggested that
most culvert replacement projects,
regardless of current serviceability, have
minimal impacts and recommended
adding language allowing a failed
culvert to be considered currently
serviceable, so that it would be eligible
for NWP 3 authorization.
While we agree that most culvert
replacements have minimal impacts, the
definition encourages maintenance to be
conducted before the structure or fill
falls into such a state of disrepair that
it can no longer be considered
serviceable. The definition is adopted as
proposed.
Discharge: We are adding a definition
of the term ‘‘discharge’’ to clarify when
a discharge of dredged or fill material
occurs for an NWP activity. This
definition clarifies that the term
‘‘discharge’’ as used in the NWPs, also
applies to any activity that causes or
results in a discharge, as defined at 33
CFR 323.2.
Enhancement. We proposed to modify
this definition to be consistent with the
wetland project type described in
Regulatory Guidance Letter 02–02 and
the definition in the Council on
Environmental Quality’s April 2006
report entitled ‘‘Conserving America’s
Wetlands 2006: Two Years of Progress
Implementing the President’s Goal.’’ We
did not receive any comments on the
proposed definition. The definition is
adopted as proposed.
Ephemeral stream. We did not
propose any changes to this definition.
Four commenters said that this
definition should address the
jurisdictional status of ephemeral
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streams. Some of these commenters said
that this definition should be removed,
because these features are not
jurisdictional. One commenter stated
that the hydrologic criteria in the
second and third sentences should be
qualified as occurring in a ‘‘typical
year.’’ One commenter suggested we
define them as features that lack a
connection to the water table and are
not waters of the United States. One
commenter said that this definition
should state that groundwater is not
typically a source of water for an
ephemeral stream.
We do not agree that it is appropriate
to state in the definition of this term that
ephemeral streams are not waters of the
United States because many ephemeral
streams are subject to Clean Water Act
jurisdiction as waters of the United
States. Further, neither the NWPs nor
this preamble are intended to address
jurisdictional issues. If an ephemeral
stream is not a water of the United
States, as defined at 33 CFR part 328,
then no Section 404 permit is required
for discharges of dredged or fill material
into it. An ephemeral stream that meets
the criteria at 33 CFR part 328 is a water
of the United States. The phrase
‘‘typical year’’ applies to the entire
definition, not just the first sentence.
Groundwater is not a source of water for
an ephemeral stream.
The definition is adopted as
proposed.
Establishment (creation). We
proposed to modify this definition to be
consistent with the wetland project type
described in Regulatory Guidance Letter
02–02 and the definition in the Council
on Environmental Quality’s April 2006
report entitled ‘‘Conserving America’s
Wetlands 2006: Two Years of Progress
Implementing the President’s Goal.’’
One commenter suggested defining
‘‘upland’’ and ‘‘deepwater site,’’ and
retaining the flexibility of the current
term ‘‘creation’’ when in-kind
mitigation is conducted. One
commenter said that the definition of
‘‘creation’’ should be retained until
questions regarding the extent of the
Corps jurisdiction are resolved. Another
commenter recommended the removal
of ‘‘deepwater’’ from this definition
because deepwater areas are aquatic
resources.
We do not believe it is necessary to
define the word ‘‘upland’’ for purposes
of the NWP program. This definition
need not specifically address
jurisdictional issues. What constitutes
an ‘‘upland’’ in contrast to an ‘‘aquatic
resource’’ will depend on the practices
in place at the time the determination is
made. We are removing the word
‘‘deepwater’’ because it is an aquatic
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resource. This definition is adopted
with the modification discussed above.
Historic property. In response to one
commenter, we are adding this term to
the ‘‘Definitions’’ section. It is adapted
from the Advisory Council on Historic
Preservation’s definition at 36 CFR
800.16(l)(1), and is provided for the
convenience of users of the NWPs.
Independent utility. We did not
receive any comments on the proposed
definition. The definition is adopted as
proposed.
Intermittent stream. We did not
receive any comments on the proposed
definition. The definition is adopted as
proposed.
Loss of waters of the United States.
We proposed to modify this definition
by replacing the phrase ‘‘above-grade,
at-grade, or below-grade fills’’ with
‘‘discharges of dredged or fill material’’
to be consistent with the definitions of
‘‘fill material’’ and ‘‘discharge of fill
material’’ issued on May 9, 2002 (67 FR
31129) at 33 CFR 323.2. We also
proposed to eliminate the sentence
stating that impacts to ephemeral
streams are not included in the linear
foot limits for stream impacts in NWPs
39, 40, 42, and 43, because of the
proposed changes to those NWPs. We
also proposed to add a sentence to this
definition to clarify that activities
exempt from section 404 permit
requirements are not included when
calculating the loss of waters of the
United States.
Three commenters stated that
activities that are not regulated should
not be included. One commenter
asserted that temporary fills should be
included as a loss because the functions
and values may not return. Six
commenters said that ephemeral
streams should not be included when
determining whether the proposed work
exceeds the acreage limit of the NWP
because the Corps lacks jurisdictional
authority in these areas. One commenter
stated that intermittent streams and
artificially created wetlands should not
be included for the same reason.
Another commenter said that the acres
of waters of the United States provided
as compensatory mitigation should
count towards the acreage limit. One
commenter stated that the loss of stream
bed should include inundation, in
addition to filling and excavation.
The first sentence of this definition
states that the permanent adverse effects
are caused by the regulated activity.
Therefore, unregulated or exempt
activities are not included when
calculating the loss of waters of the
United States. Temporary fills should
not be considered as losses of waters of
the United States, since they are
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required to be restored (see General
Condition 13, Removal of Temporary
Fills). If they are not restored properly,
then the district engineer may consider
them to be permanent losses. District
engineers may also consider permanent
losses of specific aquatic resource
functions and services when
determining if mitigation is required
(see paragraph (h) of general condition
20, Mitigation). Ephemeral streams,
intermittent streams, and man-made
wetlands that meet the regulatory
definition of ‘‘waters of the United
States’’ are included for the purposes of
this definition. As discussed in
paragraph (e) of general condition 20,
compensatory mitigation cannot be used
to decrease the acreage loss of waters of
the United States for purposes of
determining whether an NWP acreage
threshold is exceeded. Mitigation can be
used to ensure that adverse effects are
minimal. Inundation does not usually
result in the loss of stream bed. Once
the cause of inundation has been
removed, the normal water level of the
stream will return. (Note: The use of the
term ‘‘flooding’’ in the definition of
‘‘loss of waters of the United States’’
refers to the flooding of wetlands. This
conversion of wetlands to open waters
is considered a loss of waters.)
We have modified the first sentence of
this definition to make it a complete
sentence. In the third sentence of this
definition, we replaced the word
‘‘existing’’ with ‘‘jurisdictional’’ to
clarify that the measurement applies to
waters of the United States.
The definition is adopted with the
modifications discussed above.
Non-tidal wetland. We did not
propose any changes to this definition.
One commenter noted that not all
wetlands are waters of the United
States. We agree and have removed the
parenthetical expression from this
definition.
Open water. We proposed to change
this definition by adding a sentence that
describes what an ordinary high water
mark is. One commenter said that the
definition of ordinary high water mark
should be removed because there is not
common agreement regarding the
definition of this term. One commenter
recommended using the definition of
‘‘ordinary high water mark’’ from 1975
regulations. One commenter suggested
removing the language defining
‘‘ordinary high water mark’’ and making
it a separate definition. One commenter
said that this definition should not
include ephemeral waters because they
are not open waters. Another
commenter stated that this definition
should be removed, because it is not
used in the NWPs or general conditions.
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We have removed the language
defining ‘‘ordinary high water mark’’
and provided it as a separate definition
in this section. The definition is from 33
CFR 328.3(e). Ephemeral waters are
considered open waters, because they
have flowing or standing water, at least
for short periods of time. This definition
is used in NWPs 4, 27, 30 and 47, as
well as general conditions 9 and 20. The
definition is adopted with the
modification discussed above.
Ordinary high water mark. Several
commenters recommended providing a
stand alone definition of this term.
We have provided a definition of
ordinary high water mark in this
section. It is based on the definition at
33 CFR 328.3(e).
Perennial stream. We did not propose
any changes to this definition. One
commenter said that perennial flow is
dependent on time, not the water
source, and suggested modification of
this definition to state that groundwater
is usually the primary source of water,
since some perennial streams are fed by
snow melt rather than groundwater.
Another commenter stated that this
definition should recognize that some
perennial streams appear to be
intermittent because of surface and
subsurface flows in areas of karst
topography.
We acknowledge that in some parts of
the country, some perennial streams are
fed solely by snowmelt. For simplicity,
we have not included snowmelt since a
large majority of perennial streams have
groundwater as the primary source of
hydrology. When determining whether a
particular stream segment is perennial,
district engineers should consider the
source of hydrology and the normal
circumstance of that hydrology. They
will make these determinations on a
case-by-case basis. District engineers
can account for karst topography and
other geological features when
identifying perennial streams on a caseby-case basis. It is not necessary to
modify this definition to account for
such geological features.
The definition is adopted as
proposed.
Practicable. We proposed to move this
definition from the current ‘‘mitigation’’
general condition (GC 20) to the
‘‘Definitions’’ section of the NWPs. One
commenter suggested that this
definition should be modified to
include consideration of the availability
of suitable locations and
constructability, for the purposes of
mitigation.
While we agree that these are factors
involved with selecting mitigation sites,
the term ‘‘practicable’’ applies to more
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than mitigation. The definition is
adopted as proposed.
Pre-construction notification. We did
not receive any comments on the
proposed definition. The definition is
adopted as proposed.
Preservation. We proposed to modify
this definition to be consistent with the
definition for ‘‘protection/maintenance
(preservation)’’ in Regulatory Guidance
Letter 02–02 and the definition in the
Council on Environmental Quality’s
April 2006 report entitled ‘‘Conserving
America’s Wetlands 2006: Two Years of
Progress Implementing the President’s
Goal.’’ One commenter expressed
concern with the usage of ‘‘aquatic
resources’’ in the definition because it is
too expansive and should be defined
and limited to waters of the United
States.
Compensatory mitigation projects
involving preservation may include
areas that are not waters of the United
States, such as non-wetland riparian
areas next to streams or wetlands that
are not subject to Clean Water Act
jurisdiction. This definition is adopted
as proposed.
Re-establishment. We proposed to add
this definition to be consistent with the
wetland project type described in
Regulatory Guidance Letter 02–02 and
the definition in the Council on
Environmental Quality’s April 2006
report entitled ‘‘Conserving America’s
Wetlands 2006: Two Years of Progress
Implementing the President’s Goal.’’
One commenter suggested the definition
should indicate re-establishment is a
form of restoration. We do not believe
that such clarification is necessary,
since it is addressed by the definition
for restoration. The definition is
adopted as proposed.
Rehabilitation. We proposed to add
this definition to be consistent with the
wetland project type described in
Regulatory Guidance Letter 02–02 and
the definition in the Council on
Environmental Quality’s April 2006
report entitled ‘‘Conserving America’s
Wetlands 2006: Two Years of Progress
Implementing the President’s Goal.’’
One commenter suggested the definition
should state rehabilitation is a form of
restoration. We do not believe that such
clarification is necessary, since it is
addressed by the definition for
restoration. The definition is adopted as
proposed.
Restoration. We proposed to modify
this definition to be consistent with the
wetland project type described in
Regulatory Guidance Letter 02–02 and
the definition in the Council on
Environmental Quality’s April 2006
report entitled ‘‘Conserving America’s
Wetlands 2006: Two Years of Progress
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Implementing the President’s Goal.’’ We
did not receive any comments on the
proposed definition. The definition is
adopted as proposed.
Riffle and pool complex. We did not
propose any changes to this definition.
One commenter said that a riffle and
pool complex has a reoccurring pattern
of riffles and pools, and is not limited
to a single riffle and pool. One
commenter stated that this definition
should address steep gradients that are
not conducive to forming riffle and pool
complexes. One commenter said that
riffle and pool complexes are too
common to be a special aquatic site.
The definition of this term was taken
from 40 CFR 230.45. District engineers
will use their judgment to identify riffle
and pool complexes at project sites and
to distinguish between riffle and pool
complexes (which are found in areas of
moderate grades) and step-pool
complexes (which are found in areas
with steep grades, where the stream bed
material consists mostly of boulders and
large rocks). The definition is adopted
as proposed.
Riparian areas. We proposed to
replace the definition of ‘‘vegetated
buffers’’ with a definition of ‘‘riparian
areas’’ since the latter term more
accurately reflects what is normally
required as mitigation for NWP
activities where there are streams and
other open waters on a project site. Two
commenters objected to replacing the
definition of ‘‘vegetated buffers’’ with a
definition of ‘‘riparian areas’’ and said
the terms are not interchangeable. One
commenter supported the proposed
change. Another commenter said that
this definition does not match the
definition developed by the National
Research Council, and should be revised
accordingly. Five commenters said that
the use of riparian areas should be
limited to areas adjacent to streams and
other waters of the United States, other
than wetlands. They said that the
definition implies wetlands have
riparian areas due to the use of the
words ‘‘lands’’ and ‘‘waterbody,’’ which
includes wetlands by definition. Three
commenters requested that the Corps
acknowledge that not all riparian areas
are jurisdictional. One commenter said
that this definition should exclude
intermittent and ephemeral streams as
waterbodies.
We maintain that use of the term
‘‘riparian areas’’ is most appropriate,
because it is the current term used to
categorize the areas that meet the
criteria in this definition. We also
acknowledge that this definition does
not contain all the concepts provided in
the National Research Council’s
definition, but we have tried to provide
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a simpler definition for use in the NWP
program. We have modified this
definition to clarify that lands next to
wetlands are not riparian areas and to be
consistent with the definition of
‘‘waterbody.’’ We acknowledge that not
all riparian areas are subject to Clean
Water Act jurisdiction, but it is not
necessary to state that fact in this
definition. However, the use of
jurisdictional and non-jurisdictional
riparian areas as compensatory
mitigation is a legitimate method to
provide compensatory mitigation for
certain NWP activities. Riparian areas
may be established and maintained next
to intermittent streams, but in arid
regions it may not be practicable to
establish and maintain those areas next
to ephemeral streams because there may
not be sufficient water to sustain plant
communities in those areas. The
definition is adopted with the
modification discussed above.
Shellfish seeding. We have added a
definition of this term. This definition
was derived from the definition
provided in the preamble discussion for
the September 26, 2006, proposal (see
71 FR 56275).
Single and complete project. We did
not propose any changes to this
definition. One commenter suggested
that the district engineer be allowed to
use multiple NWPs for projects that
cross separate waterways. One
commenter requested the definition be
expanded to include phased projects.
The definition already allows the
district engineer the ability to use
multiple NWPs on separate waterways.
Individual phases of phased projects
can be considered as single and
complete projects only if they have
independent utility and they satisfy the
requirements of the specific NWP. We
have revised the wording of this
definition slightly to further clarify that
single and complete projects must have
independent utility and to further
clarify how multiple stream crossings
for linear projects are treated. (See also
the discussion of new general condition
28, Single and Complete Project, above.)
The definition is adopted as modified.
Stormwater management. No
comments were received on this
definition. The definition is adopted as
proposed.
Stormwater management facilities.
We did not propose any changes to this
definition. One commenter said that this
definition is too restrictive. The
definition does list examples of facilities
and some of their roles but not in an
exclusive manner. The definition is
adopted as proposed.
Stream bed. We did not propose any
changes to this definition. No comments
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were received on this definition. The
definition is adopted as proposed.
Stream channelization. We proposed
to simplify this definition, by generally
considering man-made changes to a
stream’s course, condition, capacity, or
location to be stream channelization
activities. One commenter fully
supported the definition. One
commenter requested clarification that
mitigation projects involving a ‘‘natural
channel design’’ do not constitute
‘‘stream channelization.’’ Four
commenters stated that many accepted
techniques of bank stabilization may not
satisfy the definition. As a result, one
commenter recommended removing the
word ‘‘condition’’ in order to allow
minor changes to the bank. Another
suggested modifying this definition to
state that additional work undertaken to
improve aquatic services or to increase
the net sinuosity is not stream
channelization.
Compensatory mitigation projects
involving stream restoration activities
normally would not be considered
stream channelization, since they
should not substantially disrupt normal
stream process. The restoration activity
should restore normal stream processes,
based on comparison to reference
stream systems in the vicinity of the
proposed work. We acknowledge that
some bank stabilization activities may
result in stream channelization. This
definition does not prohibit minor
changes to the stream bank. As long as
those changes are small, and do not
disrupt normal stream processes, they
would not be considered as stream
channelization. District engineers will
consider the overall net impacts,
including beneficial and adverse
impacts, to the course, condition,
capacity or location of the stream when
determining if a project will have more
than minimal impacts on normal stream
processes.
One commenter suggested inserting
‘‘natural’’ to describe the stream to
exclude ditches from being considered a
stream. District engineers will
determine on a case-by-case basis the
type of waterbody that is a stream. This
definition is adopted as proposed.
Structure. We proposed to add this
definition to the NWPs. One commenter
said that references should be made to
the structures included in NWPs 3 and
5 and that the definition ignores other
common structures like culverts and
bridges. One commenter observed that
the definition involves examples that
have fill. One commenter suggested the
definition be rewritten as: ‘‘man-made
feature constructed in an area of
regulated aquatic resources.’’
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Adding references to NWPs 3 and 5 in
this definition is unnecessary. The
examples in this definition were
adapted from 33 CFR 322.2(b) and are
not intended to be a complete list.
Bridges may constitute structures, but
bridges constructed over navigable
waters are authorized by the U.S. Coast
Guard. Culverts may consist mostly of
fill material, in accordance with the
definitions at 33 CFR 323.2. Our intent
is not to imply that structures must not
involve fill, since the construction of
structures may also involve fill
activities. We agree that structures must
be manmade and have added this
qualifier to the definition. The
definition is adopted as modified.
Tidal wetland. We did not propose
any changes to this definition. One
commenter stated that not all wetlands
are waters of the United States and
suggested adding that certain vegetation
is associated with the wetland. One
commenter stated the high tide line is
not the spring high tide line.
In the context of this definition,
wetlands subject to the ebb and flow of
the tide are waters of the United States.
We acknowledge that the high tide line
may include high tides other than
spring high tides. Therefore, we have
modified this definition by removing
the language that discusses spring high
tide lines. The definition is adopted as
modified.
Vegetated shallows. We did not
propose any changes to this definition.
No comments were received on this
definition. The definition is adopted as
proposed.
Waterbody. We proposed to modify
this definition to clarify that a
waterbody is a jurisdictional water of
the United States. We also proposed to
include a definition of ‘‘ordinary high
water mark’’ in the text of this
definition. Five commenters said that
the definition should be changed to
reflect recent judicial rulings that affect
Clean Water Act jurisdiction. They also
stated that this term cannot be used to
exert jurisdiction over areas that are not
subject to Section 404 of the Clean
Water Act.
As stated in the preamble to the
September 26, 2006, Federal Register
notice, the purpose of this definition is
not to identify which waterbodies are
jurisdictional, but to clarify how waters
of the United States are grouped into
waterbodies, especially for the purposes
of implementing 33 CFR 330.2(i), which
addresses single and complete projects
for the NWPs. We agree, and have
clarified in the definition, that only
jurisdictional waters can be waterbodies
for purposes of the NWPs.
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One commenter asked for a list of
other indicators to identify a waterbody
and exert jurisdiction. One commenter
requested that ‘‘adjacent’’ be defined.
One commenter inquired how the loss
of waters calculation will be made when
wetlands and waterbodies that are
considered a single aquatic unit.
It would not be appropriate to
promulgate, through the NWP issuance
process, a list of indicators to be used
to identify waterbodies subject to
regulatory jurisdiction. The term
‘‘adjacent’’ is defined at 33 CFR
328.3(c). District engineers will
determine, on a case-by-case basis,
when waterbodies are separate for the
purposes of identifying single and
complete projects. We note that, except
in the case of linear crossings (see
definition of ‘‘single and complete
project’’), all losses of waters of the
United States, whether separate water
bodies or not, are added together to
determine whether an activity is a single
and complete project that meets the
acreage thresholds. The definition is
adopted as proposed.
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Administrative Requirements
Regulatory Flexibility Act
One commenter objected to the
proposed certification for Regulatory
Flexibility Act compliance, and
indicated that a Regulatory Impact
Analysis is necessary. This commenter
stated that the Corps failed to analyze
the costs or other burdens that NWP
impose on small entities, and compare
those costs or burdens to alternatives.
The commenter also said that the Corps
needs to consider burdens placed on
those small entities that need to get
individual permits, since the proposed
NWPs determine who qualifies for
NWPs, as well as those who must get
individual permits. One commenter said
that an initial regulatory flexibility
analysis must be provided for public
comment, and stated that the Corps
must withdraw the proposed NWPs and
make an initial regulatory flexibility
analysis available for public review and
comment.
Our Regulatory Flexibility Act
certification was done in the context of
the statutory requirements underlying
the NWP program: the permit
requirements under Section 404 of the
Clean Water Act and Section 10 of the
Rivers and Harbors Act of 1899. The
NWPs (or any other general permits) can
only authorize activities with minimal
individual and cumulative adverse
effects on the environment; other
activities must obtain individual
permits. Because the permitted impacts
are minimal, the burden on permittees
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for obtaining coverage under the NWP is
also low. Generally, permittees are
required to submit a pre-construction
notification and adopt common sense,
low-cost practices to ensure that adverse
effects are minimal. Larger projects are
also required to provide compensatory
mitigation, but the scope of mitigation is
commensurate with the impacts of the
project and usually does not constitute
a ‘‘significant economic impact.’’
Further, such larger projects are less
likely to be undertaken by small
businesses. We continue to believe that
our certification that the NWPs will not
have a significant economic impact on
a substantial number of small entities is
appropriate. As a result, a formal
Regulatory Flexibility Analysis is not
required.
Unfunded Mandates
One commenter said that the Corps
must provide a quantified assessment of
costs and benefits of the permits (rule),
in accordance with the Unfunded
Mandates Reform Act. The costs of these
permits (mostly paperwork costs
associated with filing pre-construction
notifications, estimated at 10 hours per
pre-construction notification) do not
rise to the level of an unfunded
mandate, as defined in the statute. As a
result, it is not necessary under UMRA
to quantify the costs and benefits of this
action.
Paperwork Reduction Act
A commenter stated that the estimate
of time required to prepare a complete
pre-construction notification is too low,
because of the requirement to submit a
delineation of waters of the United
States with the pre-construction
notification.
We believe the time estimates are
accurate, because many activities will
not require a complex delineation of
waters of the United States. Most preconstruction notifications will have
simple delineations showing the
locations of waters near the project. The
estimated time is an average for all
projects.
Regional Conditioning of the
Nationwide Permits
Concurrent with this Federal Register
notice, district engineers are issuing
local public notices. In addition to the
changes to some NWPs and NWP
conditions required by the Chief of
Engineers, division and district
engineers may propose regional
conditions or propose revocation of
NWP authorization for all, some, or
portions of the NWPs. Regional
conditions may also be required by state
or Tribal water quality certification or
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for state Coastal Zone Management Act
consistency. District engineers will
announce regional conditions or
revocations by issuing local public
notices. Information on regional
conditions and revocation can be
obtained from the appropriate district
engineer, as indicated below.
Furthermore, this and additional
information can be obtained on the
Internet at https://www.usace.army.mil/
where.html#State by clicking on the
appropriate district office.
Contact Information for Corps District
Engineers
Alabama
Mobile District Engineer, ATTN:
CESAM–RD, 109 St. Joseph Street,
Mobile, AL 36602–3630.
Alaska
Alaska District Engineer, ATTN:
CEPOA–CO–R, P.O. Box 6898,
Elmendorf AFB, AK 99506–6898.
Arizona
Los Angeles District Engineer, ATTN:
CESPL–CO–R, P.O. Box 532711, Los
Angeles, CA 90053–2325.
Arkansas
Little Rock District Engineer, ATTN:
CESWL–RO, P.O. Box 867, Little
Rock, AR 72203–0867.
California
Sacramento District Engineer, ATTN:
CESPK–CO–R, 1325 J Street,
Sacramento, CA 95814–2922.
Colorado
Albuquerque District Engineer, ATTN:
CESPA–OD–R, 4101 Jefferson Plaza
NE, Albuquerque, NM 87109–3435.
Connecticut
New England District Engineer, ATTN:
CENAE–R, 696 Virginia Road,
Concord, MA 01742–2751.
Delaware
Philadelphia District Engineer, ATTN:
CENAP–OP–R, Wannamaker
Building, 100 Penn Square East
Philadelphia, PA 19107–3390.
Florida
Jacksonville District Engineer, ATTN:
CESAJ–RD, P.O. Box 4970,
Jacksonville, FL 32232–0019.
Georgia
Savannah District Engineer, ATTN:
CESAS–OP–F, P.O. Box 889,
Savannah, GA 31402–0889.
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Hawaii
Mississippi
Oregon
Honolulu District Engineer, ATTN:
CEPOH–EC–R, Building 230, Fort
Shafter, Honolulu, HI 96858–5440.
Vicksburg District Engineer, ATTN:
CEMVK–OD–F, 4155 Clay Street,
Vicksburg, MS 39183–3435.
Portland District Engineer, ATTN:
CENWP–OD–G, P.O. Box 2946,
Portland, OR 97208–2946.
Idaho
Missouri
Pennsylvania
Walla Walla District Engineer, ATTN:
CENWW–RD, 201 North Third
Avenue, Walla Walla, WA 99362–
1876.
Kansas City District Engineer, ATTN:
CENWK–OD–R, 700 Federal Building,
601 E. 12th Street, Kansas City, MO
64106–2896.
Baltimore District Engineer, ATTN:
CENAB–OP–R, P.O. Box 1715,
Baltimore, MD 21203–1715.
Illinois
Montana
Rock Island District Engineer, ATTN:
CEMVR–OD–P, P.O. Box 2004, Rock
Island, IL 61204–2004.
Omaha District Engineer, ATTN:
CENWO–OD–R, 106 South 15th
Street, Omaha, NE 68102–1618.
Indiana
Nebraska
Louisville District Engineer, ATTN:
CELRL–OP–F, P.O. Box 59, Louisville,
KY 40201–0059.
Omaha District Engineer, ATTN:
CENWO–OD–R, 106 South 15th
Street, Omaha, NE 68102–1618.
Iowa
Nevada
Rock Island District Engineer, ATTN:
CEMVR–OD–P, P.O. Box 2004, Rock
Island, IL 61204–2004.
Sacramento District Engineer, ATTN:
CESPK–CO–R, 1325 J Street,
Sacramento, CA 95814–2922.
Kansas
New Hampshire
Kansas City District Engineer, ATTN:
CENWK–OD–R, 700 Federal Building,
601 E. 12th Street, Kansas City, MO
64106–2896.
New England District Engineer, ATTN:
CENAE–R, 696 Virginia Road,
Concord, MA 01742–2751.
Nashville District Engineer, ATTN:
CELRN–OP–F, 3701 Bell Road,
Nashville, TN 37214.
Texas
Kentucky
New Jersey
Rhode Island
New England District Engineer, ATTN:
CENAE–R, 696 Virginia Road,
Concord, MA 01742–2751.
South Carolina
Charleston District Engineer, ATTN:
CESAC–CO–P, 69A Hagood Ave,
Charleston, SC 29403–5107.
South Dakota
Omaha District Engineer, ATTN:
CENWO–OD–R, 106 South 15th
Street, Omaha, NE 68102–1618.
Tennessee
Galveston District Engineer, ATTN:
CESWG–PE–R, P.O. Box 1229,
Galveston, TX 77553–1229.
Philadelphia District Engineer, ATTN:
CENAP–OP–R, Wannamaker
Building, 100 Penn Square East,
Philadelphia, PA 19107–3390.
Louisiana
New Mexico
New Orleans District Engineer, ATTN:
CEMVN–OD–S, P.O. Box 60267, New
Orleans, LA 70160–0267.
Albuquerque District Engineer, ATTN:
CESPA–OD–R, 4101 Jefferson Plaza
NE, Albuquerque, NM 87109–3435.
Maine
New York
New England District Engineer, ATTN:
CENAE–R, 696 Virginia Road,
Concord, MA 01742–2751.
New York District Engineer, ATTN:
CENAN–OP–R, 26 Federal Plaza, New
York, NY 10278–0090.
Maryland
North Carolina
Baltimore District Engineer, ATTN:
CENAB–OP–R, P.O. Box 1715,
Baltimore, MD 21203–1715.
Wilmington District Engineer, ATTN:
CESAW–RG, P.O. Box 1890,
Wilmington, NC 28402–1890.
Massachusetts
North Dakota
New England District Engineer, ATTN:
CENAE–R, 696 Virginia Road,
Concord, MA 01742–2751.
Omaha District Engineer, ATTN:
CENWO–OD–R, 106 South 15th
Street, Omaha, NE 68102–1618.
Huntington District Engineer, ATTN:
CELRH–OR–F, 502 8th Street,
Huntington, WV 25701–2070.
Michigan
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Louisville District Engineer, ATTN:
CELRL–OP–F, P.O. Box 59, Louisville,
KY 40201–0059.
Ohio
Wisconsin
Detroit District Engineer, ATTN:
CELRE–RG, P.O. Box 1027, Detroit,
MI 48231–1027.
Huntington District Engineer, ATTN:
CELRH–OR–F, 502 8th Street,
Huntington, WV 25701–2070.
St. Paul District Engineer, ATTN:
CEMVP–OP–R, 190 Fifth Street East,
St. Paul, MN 55101–1638.
Minnesota
Oklahoma
Wyoming
St. Paul District Engineer, ATTN:
CEMVP–OP–R, 190 Fifth Street East,
St. Paul, MN 55101–1638.
Tulsa District Engineer, ATTN: CESWT–
RO, 1645 S. 101st East Ave, Tulsa, OK
74128–4609.
Omaha District Engineer, ATTN:
CENWO–OD–R, 106 South 15th
Street, Omaha, NE 68102–1618.
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Utah
Sacramento District Engineer, ATTN:
CESPK–CO–R, 1325 J Street, CA
95814–2922.
Vermont
New England District Engineer, ATTN:
CENAE–R, 696 Virginia Road,
Concord, MA 01742–2751.
Virginia
Norfolk District Engineer, ATTN:
CENAO–OP–R, 803 Front Street,
Norfolk, VA 23510–1096.
Washington
Seattle District Engineer, ATTN:
CENWS–OP–RG, P.O. Box 3755,
Seattle, WA 98124–3755.
West Virginia
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District of Columbia
Baltimore District Engineer, ATTN:
CENAB–OP–R, P.O. Box 1715,
Baltimore, MD 21203–1715.
Pacific Territories (American Samoa,
Guam, & Commonwealth of the
Northern Mariana Islands)
Honolulu District Engineer, ATTN:
CEPOH–EC–R, Building 230, Fort
Shafter, Honolulu, HI 96858–5440.
Puerto Rico and Virgin Islands
Jacksonville District Engineer, ATTN:
CESAJ–RD, P.O. Box 4970,
Jacksonville, FL 32232–0019.
Administrative Requirements
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Plain Language
In compliance with the principles in
the President’s Memorandum of June 1,
1998, (63 FR 31855) regarding plain
language, this preamble is written using
plain language. The use of ‘‘we’’ in this
notice refers to the Corps. We have also
used the active voice, short sentences,
and common everyday terms except for
necessary technical terms.
Paperwork Reduction Act
These NWPs will increase the number
of permittees who are required to
submit a pre-construction notification.
The content of the pre-construction
notification is not changed from the
current NWPs, but the paperwork
burden will increase because of the
increased number of pre-construction
notifications submitted. The Corps
estimates the increased paperwork
burden at 4,500 hours per year. This is
based on an average burden to complete
and submit a pre-construction
notification of 10 hours, and an
estimated 450 additional projects that
will require pre-construction
notifications. Prospective permittees
who are required to submit a preconstruction notification for a particular
NWP, or who are requesting verification
that a particular activity qualifies for
NWP authorization, may use the current
standard Department of the Army
permit application form or submit the
required information in a letter. The
total burden for filing pre-construction
notifications is estimated at 300,000
hours per year (10 hours times 30,000
projects per year requiring preconstruction notification). In addition,
we are adding a requirement for existing
aquaculture activities using NWP 48
that do not require a pre-construction
notification to instead file a short report
indicating basic information about the
existing shellfish production operation.
The estimated burden for this new
requirement is 1,800 hours per year (900
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existing aquaculture facilities times 2
hours per report). The information in
the report is a subset of the information
required for a full pre-construction
notification.
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid
Office of Management and Budget
(OMB) control number. For the Corps
Regulatory Program under Section 10 of
the Rivers and Harbors Act of 1899,
Section 404 of the Clean Water Act, and
Section 103 of the Marine Protection,
Research and Sanctuaries Act of 1972,
the current OMB approval number for
information collection requirements is
maintained by the Corps of Engineers
(OMB approval number 0710–0003,
which expires on April 30, 2008).
Executive Order 12866
Under Executive Order 12866 (58 FR
51735, October 4, 1993), we must
determine whether the regulatory action
is ‘‘significant’’ and therefore subject to
review by OMB and the requirements of
the Executive Order. The Executive
Order defines ‘‘significant regulatory
action’’ as one that is likely to result in
a rule that may:
(1) Have an annual effect on the
economy of $100 million or more or
adversely affect in a material way the
economy, a sector of the economy,
productivity, competition, jobs, the
environment, public health or safety, or
State, local, or tribal governments or
communities;
(2) Create a serious inconsistency or
otherwise interfere with an action taken
or planned by another agency;
(3) Materially alter the budgetary
impact of entitlements, grants, user fees,
or loan programs or the rights and
obligations of recipients thereof; or
(4) Raise novel legal or policy issues
arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
Pursuant to the terms of Executive
Order 12866, we have determined that
this action is a ‘‘significant regulatory
action’’ and it was submitted to OMB for
review.
Executive Order 13132
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires the Corps to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ The issuance of NWPs
does not have federalism implications.
We do not believe that the NWPs will
have substantial direct effects on the
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States, on the relationship between the
Federal government and the States, or
on the distribution of power and
responsibilities among the various
levels of government. The NWPs will
not impose any additional substantive
obligations on State or local
governments. Therefore, Executive
Order 13132 does not apply to these
final NWPs.
Regulatory Flexibility Act, as Amended
by the Small Business Regulatory
Enforcement Fairness Act of 1996, 5
U.S.C. 601 et seq.
The Regulatory Flexibility Act
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice-and-comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of the proposed issuance and
modification of NWPs on small entities,
a small entity is defined as: (1) A small
business based on Small Business
Administration size standards; (2) a
small governmental jurisdiction that is a
government of a city, county, town,
school district, or special district with a
population of less than 50,000; or (3) a
small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
The statutes under which the Corps
issues, reissues, or modifies NWPs are
Section 404(e) of the Clean Water Act
(33 U.S.C. 1344(e)) and Section 10 of the
Rivers and Harbors Act of 1899 (33
U.S.C. 403). Under section 404,
Department of the Army (DA) permits
are required for discharges of dredged or
fill material into waters of the United
States. Under section 10, DA permits are
required for any structures or other
work that affect the course, location, or
condition of navigable waters of the
United States. Small entities proposing
to discharge dredged or fill material into
waters of the United States and/or
conduct work in navigable waters of the
United States must obtain DA permits to
conduct those activities, unless a
particular activity is exempt from those
permit requirements. Individual permits
and general permits can be issued by the
Corps to satisfy the permit requirements
of these two statutes. Nationwide
permits are a form of general permit
issued by the Chief of Engineers.
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Nationwide permits automatically
expire and become null and void if they
are not modified or reissued within five
years of their effective date (see 33 CFR
330.6(b)). Furthermore, Section 404(e) of
the Clean Water Act states that general
permits, including NWPs, can be issued
for no more than 5 years. If the current
NWPs are not reissued small entities
and other project proponents would be
required to obtain alternative forms of
DA permits (i.e., standard permits,
letters of permission, or regional general
permits) for activities involving
discharges of dredged or fill material
into waters of the United States or
structures or work in navigable waters
of the United States. Regional general
permits that authorize similar activities
as the NWPs may be available in some
geographic areas, so small entities
conducting regulated activities outside
those geographic areas would have to
obtain individual permits for activities
that require DA permits.
Nationwide permits help relieve
regulatory burdens on small entities
who need to obtain DA permits. They
provide an expedited form of
authorization, provided the project
proponent meets all terms and
conditions of the NWPs. In FY 2003, the
Corps issued 35,317 NWP verifications,
with an average processing time of 27
days. Those numbers do not include
activities that are authorized by NWP,
where the project proponent was not
required to submit a pre-construction
notification or did not voluntarily seek
verification that an activity qualified for
NWP authorization. The average
processing times for the 4,035 standard
permits and the 3,040 letters of
permission issued during FY 2003 were
187 days and 89 days, respectively. The
NWPs issued today are expected to
result in a slight increase in the
numbers of activities potentially
qualifying for NWP authorization. The
estimated numbers of activities
qualifying for NWP authorization are
provided in the decision documents that
were prepared for each NWP. The NWPs
issued today are not expected to
significantly increase cost or paperwork
burden for authorized activities (relative
to the NWPs issued in 2002), including
those conducted by small businesses.
The costs for obtaining coverage
under an NWP are low. We estimate the
average time to prepare and file a preconstruction notification, for those
activities where a pre-construction
notification is required, is 10 hours. We
do not believe this constitutes a
‘‘significant economic impact’’ on
project proponents, including small
businesses.
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Another requirement of Section 404(e)
of the Clean Water Act is that general
permits, including NWPs, authorize
only those activities that result in
minimal adverse environmental effects,
individually and cumulatively. The
terms and conditions of the NWPs, such
as acreage or linear foot limits, are
imposed to ensure that the NWPs
authorize only those activities that
result in minimal adverse effects on the
aquatic environment and other public
interest review factors. In addition to
the paperwork burden of filing a preconstruction notification, many NWPs
require that low-cost, common sense
practices be used to minimize adverse
effects. These requirements also do not
constitute ‘‘significant economic
impacts.’’
After considering the economic
impacts of these NWPs on small
entities, I certify that this action will not
have a significant impact on a
substantial number of small entities.
Small entities may obtain required DA
authorizations through the NWPs, in
cases where there are applicable NWPs
authorizing those activities and the
proposed work will result in minimal
adverse effects on the aquatic
environment and other public interest
review factors. The terms and
conditions of these NWPs will not
impose substantially higher costs on
small entities than those of the previous
NWPs. If an NWP is not available to
authorize a particular activity, then
another form of DA authorization, such
as an individual permit or regional
general permit, must be secured.
However, as noted above, we expect a
slight increase in the number of
activities than can be authorized
through NWPs, because we have issued
several new NWPs, and we are
removing some limitations in existing
NWPs and replacing them with preconstruction notification requirements
that will allow the district engineer to
judge whether any adverse effects of the
proposed project are more than
minimal, and authorize the project
under an NWP if they are not.
Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under Section 202 of the UMRA,
the agencies generally must prepare a
written statement, including a costbenefit analysis, for proposed and final
rules with ‘‘federal mandates’’ that may
result in expenditures to State, local,
and tribal governments, in the aggregate,
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or to the private sector, of $100 million
or more in any one year. Before
promulgating a rule for which a written
statement is needed, Section 205 of the
UMRA generally requires the agencies
to identify and consider a reasonable
number of regulatory alternatives and
adopt the least costly, most costeffective, or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows an agency
to adopt an alternative other than the
least costly, most cost-effective, or least
burdensome alternative if the agency
publishes with the final rule an
explanation why that alternative was
not adopted. Before an agency
establishes any regulatory requirements
that may significantly or uniquely affect
small governments, including tribal
governments, it must have developed,
under Section 203 of the UMRA, a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enabling
officials of affected small governments
to have meaningful and timely input in
the development of regulatory proposals
with significant federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
We have determined that the NWPs
issued today do not contain a Federal
mandate that may result in expenditures
of $100 million or more for State, local,
and Tribal governments, in the
aggregate, or the private sector in any
one year. The NWPs are generally
consistent with current agency practice,
do not impose new substantive
requirements and therefore do not
contain a Federal mandate that may
result in expenditures of $100 million or
more for State, local, and Tribal
governments, in the aggregate, or the
private sector in any one year.
Therefore, the NWPs issued today are
not subject to the requirements of
Sections 202 and 205 of the UMRA. For
the same reasons, we have determined
that the NWPs contains no regulatory
requirements that might significantly or
uniquely affect small governments.
Therefore, the proposed issuance and
modification of NWPs is not subject to
the requirements of Section 203 of
UMRA.
Executive Order 13045
Executive Order 13045, ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997), applies to any rule that:
(1) Is determined to be ‘‘economically
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significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
we have reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
we must evaluate the environmental
health or safety effects of the proposed
rule on children, and explain why the
regulation is preferable to other
potentially effective and reasonably
feasible alternatives.
The NWPs issued today are not
subject to this Executive Order because
they are not economically significant as
defined in Executive Order 12866. In
addition, these NWPs do not concern an
environmental or safety risk that we
have reason to believe may have a
disproportionate effect on children.
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Executive Order 13175
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 6, 2000), requires
agencies to develop an accountable
process to ensure ‘‘meaningful and
timely input by tribal officials in the
development of regulatory policies that
have tribal implications.’’ The phrase
‘‘policies that have tribal implications’’
is defined in the Executive Order to
include regulations that have
‘‘substantial direct effects on one or
more Indian tribes, on the relationship
between the Federal government and
the Indian tribes, or on the distribution
of power and responsibilities between
the Federal government and Indian
tribes.’’
The NWPs issued today do not have
tribal implications. They are generally
consistent with current agency practice
and will not have substantial direct
effects on tribal governments, on the
relationship between the Federal
government and the Indian tribes, or on
the distribution of power and
responsibilities between the Federal
government and Indian tribes.
Therefore, Executive Order 13175 does
not apply to this proposal. Corps
districts are conducting government-togovernment consultation with Indian
tribes to develop regional conditions
that help protect tribal rights and trust
resources, and to facilitate compliance
with general condition 16, Tribal Rights.
Environmental Documentation
A decision document, which includes
an environmental assessment and
Finding of No Significant Impact
(FONSI), has been prepared for each
NWP. These decision documents are
available at: https://www.regulations.gov
(docket ID number COE–2006–0005).
They are also available by contacting
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Headquarters, U.S. Army Corps of
Engineers, Operations and Regulatory
Community of Practice, 441 G Street,
NW., Washington, DC 20314–1000.
Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. We will submit a
report containing the final NWPs and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States. A major
rule cannot take effect until 60 days
after it is published in the Federal
Register. The proposed NWPs are not a
‘‘major rule’’ as defined by 5 U.S.C.
804(2).
Executive Order 12898
Executive Order 12898 requires that,
to the greatest extent practicable and
permitted by law, each Federal agency
must make achieving environmental
justice part of its mission. Executive
Order 12898 provides that each federal
agency conduct its programs, policies,
and activities that substantially affect
human health or the environment in a
manner that ensures that such programs,
policies, and activities do not have the
effect of excluding persons (including
populations) from participation in,
denying persons (including
populations) the benefits of, or
subjecting persons (including
populations) to discrimination under
such programs, policies, and activities
because of their race, color, or national
origin.
The NWPs issued today are not
expected to negatively impact any
community, and therefore are not
expected to cause any
disproportionately high and adverse
impacts to minority or low-income
communities.
Executive Order 13211
The proposed NWPs are not a
‘‘significant energy action’’ as defined in
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355, May
22, 2001) because it is not likely to have
a significant adverse effect on the
supply, distribution, or use of energy.
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Authority
We are issuing new NWPs, modifying
existing NWPs, and reissuing NWPs
without change under the authority of
Section 404(e) of the Clean Water Act
(33 U.S.C. 1344) and Section 10 of the
Rivers and Harbors Act of 1899 (33
U.S.C. 401 et seq.).
Dated: March 1, 2007.
Don T. Riley,
Major General, U.S. Army, Director of Civil
Works.
Nationwide Permits, Conditions,
Further Information, and Definitions
A. Index of Nationwide Permits,
Conditions, Further Information, and
Definitions
Nationwide Permits
1. Aids to Navigation.
2. Structures in Artificial Canals.
3. Maintenance.
4. Fish and Wildlife Harvesting,
Enhancement, and Attraction Devices
and Activities.
5. Scientific Measurement Devices.
6. Survey Activities.
7. Outfall Structures and Associated Intake
Structures.
8. Oil and Gas Structures on the Outer
Continental Shelf.
9. Structures in Fleeting and Anchorage
Areas.
10. Mooring Buoys.
11. Temporary Recreational Structures.
12. Utility Line Activities.
13. Bank Stabilization.
14. Linear Transportation Projects.
15. U.S. Coast Guard Approved Bridges.
16. Return Water From Upland Contained
Disposal Areas.
17. Hydropower Projects.
18. Minor Discharges.
19. Minor Dredging
20. Oil Spill Cleanup.
21. Surface Coal Mining Operations.
22. Removal of Vessels.
23. Approved Categorical Exclusions.
24. Indian Tribe or State Administered
Section 404 Programs.
25. Structural Discharges.
26. [Reserved].
27. Aquatic Habitat Restoration,
Establishment, and Enhancement
Activities.
28. Modifications of Existing Marinas.
29. Residential Developments.
30. Moist Soil Management for Wildlife.
31. Maintenance of Existing Flood Control
Facilities.
32. Completed Enforcement Actions.
33. Temporary Construction, Access, and
Dewatering.
34. Cranberry Production Activities.
35. Maintenance Dredging of Existing Basins.
36. Boat Ramps.
37. Emergency Watershed Protection and
Rehabilitation.
38. Cleanup of Hazardous and Toxic Waste.
39. Commercial and Institutional
Developments.
40. Agricultural Activities.
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41. Reshaping Existing Drainage Ditches.
42. Recreational Facilities.
43. Stormwater Management Facilities.
44. Mining Activities.
45. Repair of Uplands Damaged by Discrete
Events.
46. Discharges in Ditches.
47. Pipeline Safety Program Designated Time
Sensitive Inspections and Repairs.
48. Existing Commercial Shellfish
Aquaculture Activities.
49. Coal Remining Activities.
50. Underground Coal Mining Activities.
Nationwide Permit General Conditions
1. Navigation.
2. Aquatic Life Movements.
3. Spawning Areas.
4. Migratory Bird Breeding Areas.
5. Shellfish Beds.
6. Suitable Material.
7. Water Supply Intakes.
8. Adverse Effects from Impoundments.
9. Management of Water Flows.
10. Fills Within 100-Year Floodplains.
11. Equipment.
12. Soil Erosion and Sediment Controls.
13. Removal of Temporary Fills.
14. Proper Maintenance.
15. Wild and Scenic Rivers.
16. Tribal Rights.
17. Endangered Species.
18. Historic Properties.
19. Designated Critical Resource Waters.
20. Mitigation.
21. Water Quality.
22. Coastal Zone Management.
23. Regional and Case-by-Case Conditions.
24. Use of Multiple Nationwide Permits.
25. Transfer of Nationwide Permit
Verifications.
26. Compliance Certification.
27. Pre-Construction Notification.
28. Single and Complete Project.
Further Information
Definitions.
Best management practices (BMPs).
Compensatory mitigation.
Currently serviceable.
Discharge.
Enhancement.
Ephemeral stream.
Establishment (creation).
Historic property.
Independent utility.
Intermittent stream.
Loss of waters of the United States.
Non-tidal wetland.
Open water.
Ordinary high water mark.
Perennial stream.
Practicable.
Pre-construction notification.
Preservation.
Re-establishment.
Rehabilitation.
Restoration.
Riffle and pool complex.
Riparian areas.
Shellfish seeding.
Single and complete project.
Stormwater management.
Stormwater management facilities.
Stream bed.
Stream channelization.
Structure.
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Tidal wetland.
Vegetated shallows.
Waterbody.
B. Nationwide Permits
1. Aids to Navigation. The placement
of aids to navigation and regulatory
markers which are approved by and
installed in accordance with the
requirements of the U.S. Coast Guard
(see 33 CFR, chapter I, subchapter C,
part 66). (Section 10)
2. Structures in Artificial Canals.
Structures constructed in artificial
canals within principally residential
developments where the connection of
the canal to a navigable water of the
United States has been previously
authorized (see 33 CFR 322.5(g)).
(Section 10)
3. Maintenance. (a) The repair,
rehabilitation, or replacement of any
previously authorized, currently
serviceable, structure, or fill, or of any
currently serviceable structure or fill
authorized by 33 CFR 330.3, provided
that the structure or fill is not to be put
to uses differing from those uses
specified or contemplated for it in the
original permit or the most recently
authorized modification. Minor
deviations in the structure’s
configuration or filled area, including
those due to changes in materials,
construction techniques, or current
construction codes or safety standards
that are necessary to make the repair,
rehabilitation, or replacement are
authorized. This NWP authorizes the
repair, rehabilitation, or replacement of
those structures or fills destroyed or
damaged by storms, floods, fire or other
discrete events, provided the repair,
rehabilitation, or replacement is
commenced, or is under contract to
commence, within two years of the date
of their destruction or damage. In cases
of catastrophic events, such as
hurricanes or tornadoes, this two-year
limit may be waived by the district
engineer, provided the permittee can
demonstrate funding, contract, or other
similar delays.
(b) This NWP also authorizes the
removal of accumulated sediments and
debris in the vicinity of and within
existing structures (e.g., bridges,
culverted road crossings, water intake
structures, etc.) and the placement of
new or additional riprap to protect the
structure. The removal of sediment is
limited to the minimum necessary to
restore the waterway in the immediate
vicinity of the structure to the
approximate dimensions that existed
when the structure was built, but cannot
extend further than 200 feet in any
direction from the structure. This 200
foot limit does not apply to maintenance
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dredging to remove accumulated
sediments blocking or restricting outfall
and intake structures or to maintenance
dredging to remove accumulated
sediments from canals associated with
outfall and intake structures. All
dredged or excavated materials must be
deposited and retained in an upland
area unless otherwise specifically
approved by the district engineer under
separate authorization. The placement
of riprap must be the minimum
necessary to protect the structure or to
ensure the safety of the structure. Any
bank stabilization measures not directly
associated with the structure will
require a separate authorization from
the district engineer.
(c) This NWP also authorizes
temporary structures, fills, and work
necessary to conduct the maintenance
activity. Appropriate measures must be
taken to maintain normal downstream
flows and minimize flooding to the
maximum extent practicable, when
temporary structures, work, and
discharges, including cofferdams, are
necessary for construction activities,
access fills, or dewatering of
construction sites. Temporary fills must
consist of materials, and be placed in a
manner, that will not be eroded by
expected high flows. Temporary fills
must be removed in their entirety and
the affected areas returned to preconstruction elevations. The areas
affected by temporary fills must be
revegetated, as appropriate.
(d) This NWP does not authorize
maintenance dredging for the primary
purpose of navigation or beach
restoration. This NWP does not
authorize new stream channelization or
stream relocation projects.
Notification: For activities authorized
by paragraph (b) of this NWP, the
permittee must submit a preconstruction notification to the district
engineer prior to commencing the
activity (see general condition 27).
Where maintenance dredging is
proposed, the pre-construction
notification must include information
regarding the original design capacities
and configurations of the outfalls,
intakes, small impoundments, and
canals. (Sections 10 and 404)
Note: This NWP authorizes the repair,
rehabilitation, or replacement of any
previously authorized structure or fill that
does not qualify for the Clean Water Act
Section 404(f) exemption for maintenance.
4. Fish and Wildlife Harvesting,
Enhancement, and Attraction Devices
and Activities. Fish and wildlife
harvesting devices and activities such as
pound nets, crab traps, crab dredging,
eel pots, lobster traps, duck blinds, and
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clam and oyster digging, and small fish
attraction devices such as open water
fish concentrators (sea kites, etc.). This
NWP does not authorize artificial reefs
or impoundments and semiimpoundments of waters of the United
States for the culture or holding of
motile species such as lobster, or the use
of covered oyster trays or clam racks.
(Sections 10 and 404)
5. Scientific Measurement Devices.
Devices, whose purpose is to measure
and record scientific data, such as staff
gages, tide gages, water recording
devices, water quality testing and
improvement devices, and similar
structures. Small weirs and flumes
constructed primarily to record water
quantity and velocity are also
authorized provided the discharge is
limited to 25 cubic yards. (Sections 10
and 404)
6. Survey Activities. Survey activities,
such as core sampling, seismic
exploratory operations, plugging of
seismic shot holes and other
exploratory-type bore holes, exploratory
trenching, soil surveys, sampling, and
historic resources surveys. For the
purposes of this NWP, the term
‘‘exploratory trenching’’ means
mechanical land clearing of the upper
soil profile to expose bedrock or
substrate, for the purpose of mapping or
sampling the exposed material. The area
in which the exploratory trench is dug
must be restored to its pre-construction
elevation upon completion of the work.
In wetlands, the top 6 to 12 inches of
the trench should normally be
backfilled with topsoil from the trench.
This NWP authorizes the construction
of temporary pads, provided the
discharge does not exceed 25 cubic
yards. Discharges and structures
associated with the recovery of historic
resources are not authorized by this
NWP. Drilling and the discharge of
excavated material from test wells for
oil and gas exploration are not
authorized by this NWP; the plugging of
such wells is authorized. Fill placed for
roads and other similar activities is not
authorized by this NWP. The NWP does
not authorize any permanent structures.
The discharge of drilling mud and
cuttings may require a permit under
Section 402 of the Clean Water Act.
(Sections 10 and 404)
7. Outfall Structures and Associated
Intake Structures. Activities related to
the construction or modification of
outfall structures and associated intake
structures, where the effluent from the
outfall is authorized, conditionally
authorized, or specifically exempted by,
or that are otherwise in compliance with
regulations issued under the National
Pollutant Discharge Elimination System
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Program (Section 402 of the Clean Water
Act). The construction of intake
structures is not authorized by this
NWP, unless they are directly associated
with an authorized outfall structure.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Sections 10 and 404)
8. Oil and Gas Structures on the Outer
Continental Shelf. Structures for the
exploration, production, and
transportation of oil, gas, and minerals
on the outer continental shelf within
areas leased for such purposes by the
Department of the Interior, Minerals
Management Service. Such structures
shall not be placed within the limits of
any designated shipping safety fairway
or traffic separation scheme, except
temporary anchors that comply with the
fairway regulations in 33 CFR 322.5(l).
The district engineer will review such
proposals to ensure compliance with the
provisions of the fairway regulations in
33 CFR 322.5(l). Any Corps review
under this NWP will be limited to the
effects on navigation and national
security in accordance with 33 CFR
322.5(f). Such structures will not be
placed in established danger zones or
restricted areas as designated in 33 CFR
part 334, nor will such structures be
permitted in EPA or Corps designated
dredged material disposal areas.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Section 10)
9. Structures in Fleeting and
Anchorage Areas. Structures, buoys,
floats and other devices placed within
anchorage or fleeting areas to facilitate
moorage of vessels where the U.S. Coast
Guard has established such areas for
that purpose. (Section 10)
10. Mooring Buoys. Non-commercial,
single-boat, mooring buoys. (Section 10)
11. Temporary Recreational
Structures. Temporary buoys, markers,
small floating docks, and similar
structures placed for recreational use
during specific events such as water
skiing competitions and boat races or
seasonal use, provided that such
structures are removed within 30 days
after use has been discontinued. At
Corps of Engineers reservoirs, the
reservoir manager must approve each
buoy or marker individually. (Section
10)
12. Utility Line Activities. Activities
required for the construction,
maintenance, repair, and removal of
utility lines and associated facilities in
waters of the United States, provided
the activity does not result in the loss
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of greater than 1⁄2 acre of waters of the
United States.
Utility lines: This NWP authorizes the
construction, maintenance, or repair of
utility lines, including outfall and
intake structures, and the associated
excavation, backfill, or bedding for the
utility lines, in all waters of the United
States, provided there is no change in
pre-construction contours. A ‘‘utility
line’’ is defined as any pipe or pipeline
for the transportation of any gaseous,
liquid, liquescent, or slurry substance,
for any purpose, and any cable, line, or
wire for the transmission for any
purpose of electrical energy, telephone,
and telegraph messages, and radio and
television communication. The term
‘‘utility line’’ does not include activities
that drain a water of the United States,
such as drainage tile or french drains,
but it does apply to pipes conveying
drainage from another area.
Material resulting from trench
excavation may be temporarily sidecast
into waters of the United States for no
more than three months, provided the
material is not placed in such a manner
that it is dispersed by currents or other
forces. The district engineer may extend
the period of temporary side casting for
no more than a total of 180 days, where
appropriate. In wetlands, the top 6 to 12
inches of the trench should normally be
backfilled with topsoil from the trench.
The trench cannot be constructed or
backfilled in such a manner as to drain
waters of the United States (e.g.,
backfilling with extensive gravel layers,
creating a french drain effect). Any
exposed slopes and stream banks must
be stabilized immediately upon
completion of the utility line crossing of
each waterbody.
Utility line substations: This NWP
authorizes the construction,
maintenance, or expansion of substation
facilities associated with a power line or
utility line in non-tidal waters of the
United States, provided the activity, in
combination with all other activities
included in one single and complete
project, does not result in the loss of
greater than 1⁄2 acre of waters of the
United States. This NWP does not
authorize discharges into non-tidal
wetlands adjacent to tidal waters of the
United States to construct, maintain, or
expand substation facilities.
Foundations for overhead utility line
towers, poles, and anchors: This NWP
authorizes the construction or
maintenance of foundations for
overhead utility line towers, poles, and
anchors in all waters of the United
States, provided the foundations are the
minimum size necessary and separate
footings for each tower leg (rather than
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a larger single pad) are used where
feasible.
Access roads: This NWP authorizes
the construction of access roads for the
construction and maintenance of utility
lines, including overhead power lines
and utility line substations, in non-tidal
waters of the United States, provided
the total discharge from a single and
complete project does not cause the loss
of greater than 1⁄2-acre of non-tidal
waters of the United States. This NWP
does not authorize discharges into nontidal wetlands adjacent to tidal waters
for access roads. Access roads must be
the minimum width necessary (see Note
2, below). Access roads must be
constructed so that the length of the
road minimizes any adverse effects on
waters of the United States and must be
as near as possible to pre-construction
contours and elevations (e.g., at grade
corduroy roads or geotextile/gravel
roads). Access roads constructed above
pre-construction contours and
elevations in waters of the United States
must be properly bridged or culverted to
maintain surface flows.
This NWP may authorize utility lines
in or affecting navigable waters of the
United States even if there is no
associated discharge of dredged or fill
material (See 33 CFR part 322).
Overhead utility lines constructed over
section 10 waters and utility lines that
are routed in or under section 10 waters
without a discharge of dredged or fill
material require a section 10 permit.
This NWP also authorizes temporary
structures, fills, and work necessary to
conduct the utility line activity.
Appropriate measures must be taken to
maintain normal downstream flows and
minimize flooding to the maximum
extent practicable, when temporary
structures, work, and discharges,
including cofferdams, are necessary for
construction activities, access fills, or
dewatering of construction sites.
Temporary fills must consist of
materials, and be placed in a manner,
that will not be eroded by expected high
flows. Temporary fills must be removed
in their entirety and the affected areas
returned to pre-construction elevations.
The areas affected by temporary fills
must be revegetated, as appropriate.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity if any of the
following criteria are met: (1) The
activity involves mechanized land
clearing in a forested wetland for the
utility line right-of-way; (2) a section 10
permit is required; (3) the utility line in
waters of the United States, excluding
overhead lines, exceeds 500 feet; (4) the
utility line is placed within a
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jurisdictional area (i.e., water of the
United States), and it runs parallel to a
stream bed that is within that
jurisdictional area; (5) discharges that
result in the loss of greater than 1⁄10-acre
of waters of the United States; (6)
permanent access roads are constructed
above grade in waters of the United
States for a distance of more than 500
feet; or (7) permanent access roads are
constructed in waters of the United
States with impervious materials. (See
general condition 27.) (Sections 10 and
404)
Note 1: Where the proposed utility line is
constructed or installed in navigable waters
of the United States (i.e., section 10 waters),
copies of the pre-construction notification
and NWP verification will be sent by the
Corps to the National Oceanic and
Atmospheric Administration (NOAA),
National Ocean Service (NOS), for charting
the utility line to protect navigation.
Note 2: Access roads used for both
construction and maintenance may be
authorized, provided they meet the terms and
conditions of this NWP. Access roads used
solely for construction of the utility line must
be removed upon completion of the work,
accordance with the requirements for
temporary fills.
Note 3: Pipes or pipelines used to transport
gaseous, liquid, liquescent, or slurry
substances over navigable waters of the
United States are considered to be bridges,
not utility lines, and may require a permit
from the U.S. Coast Guard pursuant to
Section 9 of the Rivers and Harbors Act of
1899. However, any discharges of dredged or
fill material into waters of the United States
associated with such pipelines will require a
section 404 permit (see NWP 15).
13. Bank Stabilization. Bank
stabilization activities necessary for
erosion prevention, provided the
activity meets all of the following
criteria:
(a) No material is placed in excess of
the minimum needed for erosion
protection;
(b) The activity is no more than 500
feet in length along the bank, unless this
criterion is waived in writing by the
district engineer;
(c) The activity will not exceed an
average of one cubic yard per running
foot placed along the bank below the
plane of the ordinary high water mark
or the high tide line, unless this
criterion is waived in writing by the
district engineer;
(d) The activity does not involve
discharges of dredged or fill material
into special aquatic sites, unless this
criterion is waived in writing by the
district engineer;
(e) No material is of the type, or is
placed in any location, or in any
manner, to impair surface water flow
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into or out of any water of the United
States;
(f) No material is placed in a manner
that will be eroded by normal or
expected high flows (properly anchored
trees and treetops may be used in low
energy areas); and, (g) The activity is not
a stream channelization activity.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity if the bank
stabilization activity: (1) Involves
discharges into special aquatic sites; (2)
is in excess of 500 feet in length; or (3)
will involve the discharge of greater
than an average of one cubic yard per
running foot along the bank below the
plane of the ordinary high water mark
or the high tide line. (See general
condition 27.) (Sections 10 and 404)
14. Linear Transportation Projects.
Activities required for the construction,
expansion, modification, or
improvement of linear transportation
projects (e.g., roads, highways, railways,
trails, airport runways, and taxiways) in
waters of the United States. For linear
transportation projects in non-tidal
waters, the discharge cannot cause the
loss of greater than 1⁄2-acre of waters of
the United States. For linear
transportation projects in tidal waters,
the discharge cannot cause the loss of
greater than 1⁄3-acre of waters of the
United States. Any stream channel
modification, including bank
stabilization, is limited to the minimum
necessary to construct or protect the
linear transportation project; such
modifications must be in the immediate
vicinity of the project.
This NWP also authorizes temporary
structures, fills, and work necessary to
construct the linear transportation
project. Appropriate measures must be
taken to maintain normal downstream
flows and minimize flooding to the
maximum extent practicable, when
temporary structures, work, and
discharges, including cofferdams, are
necessary for construction activities,
access fills, or dewatering of
construction sites. Temporary fills must
consist of materials, and be placed in a
manner, that will not be eroded by
expected high flows. Temporary fills
must be removed in their entirety and
the affected areas returned to preconstruction elevations. The areas
affected by temporary fills must be
revegetated, as appropriate.
This NWP cannot be used to authorize
non-linear features commonly
associated with transportation projects,
such as vehicle maintenance or storage
buildings, parking lots, train stations, or
aircraft hangars.
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Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity if: (1) The loss
of waters of the United States exceeds
1⁄10 acre; or (2) there is a discharge in
a special aquatic site, including
wetlands. (See general condition 27.)
(Sections 10 and 404)
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Note: Some discharges for the construction
of farm roads or forest roads, or temporary
roads for moving mining equipment, may
qualify for an exemption under Section 404(f)
of the Clean Water Act (see 33 CFR 323.4).
15. U.S. Coast Guard Approved
Bridges. Discharges of dredged or fill
material incidental to the construction
of bridges across navigable waters of the
United States, including cofferdams,
abutments, foundation seals, piers, and
temporary construction and access fills,
provided such discharges have been
authorized by the U.S. Coast Guard as
part of the bridge permit. Causeways
and approach fills are not included in
this NWP and will require a separate
section 404 permit. (Section 404)
16. Return Water From Upland
Contained Disposal Areas. Return water
from an upland contained dredged
material disposal area. The return water
from a contained disposal area is
administratively defined as a discharge
of dredged material by 33 CFR 323.2(d),
even though the disposal itself occurs
on the upland and does not require a
section 404 permit. This NWP satisfies
the technical requirement for a section
404 permit for the return water where
the quality of the return water is
controlled by the state through the
section 401 certification procedures.
The dredging activity may require a
section 404 permit (33 CFR 323.2(d)),
and will require a section 10 permit if
located in navigable waters of the
United States. (Section 404)
17. Hydropower Projects. Discharges
of dredged or fill material associated
with hydropower projects having: (a)
Less than 5000 kW of total generating
capacity at existing reservoirs, where
the project, including the fill, is licensed
by the Federal Energy Regulatory
Commission (FERC) under the Federal
Power Act of 1920, as amended; or (b)
a licensing exemption granted by the
FERC pursuant to Section 408 of the
Energy Security Act of 1980 (16 U.S.C.
2705 and 2708) and Section 30 of the
Federal Power Act, as amended.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Section 404)
18. Minor Discharges. Minor
discharges of dredged or fill material
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into all waters of the United States,
provided the activity meets all of the
following criteria:
(a) The quantity of discharged
material and the volume of area
excavated do not exceed 25 cubic yards
below the plane of the ordinary high
water mark or the high tide line;
(b) The discharge will not cause the
loss of more than 1/10 acre of waters of
the United States; and
(c) The discharge is not placed for the
purpose of a stream diversion.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity if: (1) The
discharge or the volume of area
excavated exceeds 10 cubic yards below
the plane of the ordinary high water
mark or the high tide line, or (2) the
discharge is in a special aquatic site,
including wetlands. (See general
condition 27.) (Sections 10 and 404)
19. Minor Dredging. Dredging of no
more than 25 cubic yards below the
plane of the ordinary high water mark
or the mean high water mark from
navigable waters of the United States
(i.e., section 10 waters). This NWP does
not authorize the dredging or
degradation through siltation of coral
reefs, sites that support submerged
aquatic vegetation (including sites
where submerged aquatic vegetation is
documented to exist but may not be
present in a given year), anadromous
fish spawning areas, or wetlands, or the
connection of canals or other artificial
waterways to navigable waters of the
United States (see 33 CFR 322.5(g)).
(Sections 10 and 404)
20. Oil Spill Cleanup. Activities
required for the containment and
cleanup of oil and hazardous substances
that are subject to the National Oil and
Hazardous Substances Pollution
Contingency Plan (40 CFR part 300)
provided that the work is done in
accordance with the Spill Control and
Countermeasure Plan required by 40
CFR 112.3 and any existing state
contingency plan and provided that the
Regional Response Team (if one exists
in the area) concurs with the proposed
containment and cleanup action. This
NWP also authorizes activities required
for the cleanup of oil releases in waters
of the United States from electrical
equipment that are governed by EPA’s
polychlorinated biphenyl spill response
regulations at 40 CFR part 761. (Sections
10 and 404)
21. Surface Coal Mining Operations.
Discharges of dredged or fill material
into waters of the United States
associated with surface coal mining and
reclamation operations provided the
activities are already authorized, or are
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currently being processed as part of an
integrated permit processing procedure,
by the Department of Interior (DOI),
Office of Surface Mining (OSM), or by
states with approved programs under
Title V of the Surface Mining Control
and Reclamation Act of 1977.
Notification: The permittee must
submit a pre-construction notification to
the district engineer and receive written
authorization prior to commencing the
activity. (See general condition 27.)
(Sections 10 and 404)
22. Removal of Vessels. Temporary
structures or minor discharges of
dredged or fill material required for the
removal of wrecked, abandoned, or
disabled vessels, or the removal of manmade obstructions to navigation. This
NWP does not authorize maintenance
dredging, shoal removal, or riverbank
snagging.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity if: (1) The
vessel is listed or eligible for listing in
the National Register of Historic Places;
or (2) the activity is conducted in a
special aquatic site, including coral
reefs and wetlands. (See general
condition 27.) If condition 1 above is
triggered, the permittee cannot
commence the activity until informed
by the district engineer that compliance
with the ‘‘Historic Properties’’ general
condition is completed. (Sections 10
and 404)
Note 1: If a removed vessel is disposed of
in waters of the United States, a permit from
the U.S. EPA may be required (see 40 CFR
229.3). If a Department of the Army permit
is required for vessel disposal in waters of
the United States, separate authorization will
be required.
Note 2: Compliance with general condition
17, Endangered Species, and general
condition 18, Historic Properties, is required
for all NWPs. The concern with historic
properties is emphasized in the notification
requirements for this NWP because of the
likelihood that submerged vessels may be
historic properties.
23. Approved Categorical Exclusions.
Activities undertaken, assisted,
authorized, regulated, funded, or
financed, in whole or in part, by another
Federal agency or department where:
(a) That agency or department has
determined, pursuant to the Council on
Environmental Quality’s implementing
regulations for the National
Environmental Policy Act (40 CFR part
1500 et seq.), that the activity is
categorically excluded from
environmental documentation, because
it is included within a category of
actions which neither individually nor
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cumulatively have a significant effect on
the human environment; and
(b) The Office of the Chief of
Engineers (Attn: CECW–CO) has
concurred with that agency’s or
department’s determination that the
activity is categorically excluded and
approved the activity for authorization
under NWP 23.
The Office of the Chief of Engineers
may require additional conditions,
including pre-construction notification,
for authorization of an agency’s
categorical exclusions under this NWP.
Notification: Certain categorical
exclusions approved for authorization
under this NWP require the permittee to
submit a pre-construction notification to
the district engineer prior to
commencing the activity (see general
condition 27). The activities that require
pre-construction notification are listed
in the appropriate Regulatory Guidance
Letters. (Sections 10 and 404)
Note: The agency or department may
submit an application for an activity believed
to be categorically excluded to the Office of
the Chief of Engineers (Attn: CECW–CO).
Prior to approval for authorization under this
NWP of any agency’s activity, the Office of
the Chief of Engineers will solicit public
comment. As of the date of issuance of this
NWP, agencies with approved categorical
exclusions are the: Bureau of Reclamation,
Federal Highway Administration, and U.S.
Coast Guard. Activities approved for
authorization under this NWP as of the date
of this notice are found in Corps Regulatory
Guidance Letter 05–07, which is available at:
https://www.usace.army.mil/inet/functions/
cw/cecwo/reg/rglsindx.htm. Any future
approved categorical exclusions will be
announced in Regulatory Guidance Letters
and posted on this same Web site.
24. Indian Tribe or State
Administered Section 404 Programs.
Any activity permitted by a state or
Indian Tribe administering its own
section 404 permit program pursuant to
33 U.S.C. 1344(g)–(l) is permitted
pursuant to Section 10 of the Rivers and
Harbors Act of 1899. (Section 10)
Note 1: As of the date of the promulgation
of this NWP, only New Jersey and Michigan
administer their own section 404 permit
programs.
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Note 2: Those activities that do not involve
an Indian Tribe or State section 404 permit
are not included in this NWP, but certain
structures will be exempted by Section 154
of Pub. L. 94–587, 90 Stat. 2917 (33 U.S.C.
591) (see 33 CFR 322.3(a)(2)).
25. Structural Discharges. Discharges
of material such as concrete, sand, rock,
etc., into tightly sealed forms or cells
where the material will be used as a
structural member for standard pile
supported structures, such as bridges,
transmission line footings, and
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walkways, or for general navigation,
such as mooring cells, including the
excavation of bottom material from
within the form prior to the discharge of
concrete, sand, rock, etc. This NWP
does not authorize filled structural
members that would support buildings,
building pads, homes, house pads,
parking areas, storage areas and other
such structures. The structure itself may
require a section 10 permit if located in
navigable waters of the United States.
(Section 404)
26. [Reserved]
27. Aquatic Habitat Restoration,
Establishment, and Enhancement
Activities. Activities in waters of the
United States associated with the
restoration, enhancement, and
establishment of tidal and non-tidal
wetlands and riparian areas and the
restoration and enhancement of nontidal streams and other non-tidal open
waters, provided those activities result
in net increases in aquatic resource
functions and services.
To the extent that a Corps permit is
required, activities authorized by this
NWP include, but are not limited to: the
removal of accumulated sediments; the
installation, removal, and maintenance
of small water control structures, dikes,
and berms; the installation of current
deflectors; the enhancement,
restoration, or establishment of riffle
and pool stream structure; the
placement of in-stream habitat
structures; modifications of the stream
bed and/or banks to restore or establish
stream meanders; the backfilling of
artificial channels and drainage ditches;
the removal of existing drainage
structures; the construction of small
nesting islands; the construction of open
water areas; the construction of oyster
habitat over unvegetated bottom in tidal
waters; shellfish seeding; activities
needed to reestablish vegetation,
including plowing or discing for seed
bed preparation and the planting of
appropriate wetland species;
mechanized land clearing to remove
non-native invasive, exotic, or nuisance
vegetation; and other related activities.
Only native plant species should be
planted at the site.
This NWP authorizes the relocation of
non-tidal waters, including non-tidal
wetlands and streams, on the project
site provided there are net increases in
aquatic resource functions and services.
Except for the relocation of non-tidal
waters on the project site, this NWP
does not authorize the conversion of a
stream or natural wetlands to another
aquatic habitat type (e.g., stream to
wetland or vice versa) or uplands. This
NWP does not authorize stream
channelization. This NWP does not
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authorize the relocation of tidal waters
or the conversion of tidal waters,
including tidal wetlands, to other
aquatic uses, such as the conversion of
tidal wetlands into open water
impoundments.
Reversion. For enhancement,
restoration, and establishment activities
conducted: (1) In accordance with the
terms and conditions of a binding
wetland enhancement, restoration, or
establishment agreement between the
landowner and the U.S. Fish and
Wildlife Service (FWS), the Natural
Resources Conservation Service (NRCS),
the Farm Service Agency (FSA), the
National Marine Fisheries Service
(NMFS), the National Ocean Service
(NOS), or their designated state
cooperating agencies; (2) as voluntary
wetland restoration, enhancement, and
establishment actions documented by
the NRCS or USDA Technical Service
Provider pursuant to NRCS Field Office
Technical Guide standards; or (3) on
reclaimed surface coal mine lands, in
accordance with a Surface Mining
Control and Reclamation Act permit
issued by the OSM or the applicable
state agency, this NWP also authorizes
any future discharge of dredged or fill
material associated with the reversion of
the area to its documented prior
condition and use (i.e., prior to the
restoration, enhancement, or
establishment activities). The reversion
must occur within five years after
expiration of a limited term wetland
restoration or establishment agreement
or permit, and is authorized in these
circumstances even if the discharge
occurs after this NWP expires. The fiveyear reversion limit does not apply to
agreements without time limits reached
between the landowner and the FWS,
NRCS, FSA, NMFS, NOS, or an
appropriate state cooperating agency.
This NWP also authorizes discharges of
dredged or fill material in waters of the
United States for the reversion of
wetlands that were restored, enhanced,
or established on prior-converted
cropland that has not been abandoned
or on uplands, in accordance with a
binding agreement between the
landowner and NRCS, FSA, FWS, or
their designated state cooperating
agencies (even though the restoration,
enhancement, or establishment activity
did not require a section 404 permit).
The prior condition will be documented
in the original agreement or permit, and
the determination of return to prior
conditions will be made by the Federal
agency or appropriate state agency
executing the agreement or permit.
Before conducting any reversion activity
the permittee or the appropriate Federal
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or state agency must notify the district
engineer and include the documentation
of the prior condition. Once an area has
reverted to its prior physical condition,
it will be subject to whatever the Corps
Regulatory requirements are applicable
to that type of land at the time. The
requirement that the activity result in a
net increase in aquatic resource
functions and services does not apply to
reversion activities meeting the above
conditions. Except for the activities
described above, this NWP does not
authorize any future discharge of
dredged or fill material associated with
the reversion of the area to its prior
condition. In such cases a separate
permit would be required for any
reversion.
Reporting: For those activities that do
not require pre-construction
notification, the permittee must submit
to the district engineer a copy of: (1) The
binding wetland enhancement,
restoration, or establishment agreement,
or a project description, including
project plans and location map; (2) the
NRCS or USDA Technical Service
Provider documentation for the
voluntary wetland restoration,
enhancement, or establishment action;
or (3) the SMCRA permit issued by OSM
or the applicable state agency. These
documents must be submitted to the
district engineer at least 30 days prior to
commencing activities in waters of the
United States authorized by this NWP.
Notification. The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity (see general
condition 27), except for the following
activities:
(1) Activities conducted on nonFederal public lands and private lands,
in accordance with the terms and
conditions of a binding wetland
enhancement, restoration, or
establishment agreement between the
landowner and the U.S. FWS, NRCS,
FSA, NMFS, NOS, or their designated
state cooperating agencies;
(2) Voluntary wetland restoration,
enhancement, and establishment actions
documented by the NRCS or USDA
Technical Service Provider pursuant to
NRCS Field Office Technical Guide
standards; or
(3) The reclamation of surface coal
mine lands, in accordance with an
SMCRA permit issued by the OSM or
the applicable state agency.
However, the permittee must submit a
copy of the appropriate documentation.
(Sections 10 and 404)
Note: This NWP can be used to authorize
compensatory mitigation projects, including
mitigation banks and in-lieu fee programs.
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However, this NWP does not authorize the
reversion of an area used for a compensatory
mitigation project to its prior condition, since
compensatory mitigation is generally
intended to be permanent.
28. Modifications of Existing Marinas.
Reconfiguration of existing docking
facilities within an authorized marina
area. No dredging, additional slips, dock
spaces, or expansion of any kind within
waters of the United States is authorized
by this NWP. (Section 10)
29. Residential Developments.
Discharges of dredged or fill material
into non-tidal waters of the United
States for the construction or expansion
of a single residence, a multiple unit
residential development, or a residential
subdivision. This NWP authorizes the
construction of building foundations
and building pads and attendant
features that are necessary for the use of
the residence or residential
development. Attendant features may
include but are not limited to roads,
parking lots, garages, yards, utility lines,
storm water management facilities,
septic fields, and recreation facilities
such as playgrounds, playing fields, and
golf courses (provided the golf course is
an integral part of the residential
development).
The discharge must not cause the loss
of greater than 1⁄2-acre of non-tidal
waters of the United States, including
the loss of no more than 300 linear feet
of stream bed, unless for intermittent
and ephemeral stream beds this 300
linear foot limit is waived in writing by
the district engineer. This NWP does not
authorize discharges into non-tidal
wetlands adjacent to tidal waters.
Subdivisions: For residential
subdivisions, the aggregate total loss of
waters of United States authorized by
this NWP cannot exceed 1/2 acre. This
includes any loss of waters of the
United States associated with
development of individual subdivision
lots.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Sections 10 and 404)
30. Moist Soil Management for
Wildlife. Discharges of dredged or fill
material into non-tidal waters of the
United States and maintenance
activities that are associated with moist
soil management for wildlife for the
purpose of continuing ongoing, sitespecific, wildlife management activities
where soil manipulation is used to
manage habitat and feeding areas for
wildlife. Such activities include, but are
not limited to, plowing or discing to
impede succession, preparing seed beds,
or establishing fire breaks. Sufficient
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riparian areas must be maintained
adjacent to all open water bodies,
including streams to preclude water
quality degradation due to erosion and
sedimentation. This NWP does not
authorize the construction of new dikes,
roads, water control structures, or
similar features associated with the
management areas. The activity must
not result in a net loss of aquatic
resource functions and services. This
NWP does not authorize the conversion
of wetlands to uplands, impoundments,
or other open water bodies. (Section
404).
Note: The repair, maintenance, or
replacement of existing water control
structures or the repair or maintenance of
dikes may be authorized by NWP 3. Some
such activities may qualify for an exemption
under Section 404(f) of the Clean Water Act
(see 33 CFR 323.4).
31. Maintenance of Existing Flood
Control Facilities. Discharges of dredged
or fill material resulting from activities
associated with the maintenance of
existing flood control facilities,
including debris basins, retention/
detention basins, levees, and channels
that: (i) were previously authorized by
the Corps by individual permit, general
permit, by 33 CFR 330.3, or did not
require a permit at the time they were
constructed, or (ii) were constructed by
the Corps and transferred to a nonFederal sponsor for operation and
maintenance. Activities authorized by
this NWP are limited to those resulting
from maintenance activities that are
conducted within the ‘‘maintenance
baseline,’’ as described in the definition
below. Discharges of dredged or fill
materials associated with maintenance
activities in flood control facilities in
any watercourse that have previously
been determined to be within the
maintenance baseline are authorized
under this NWP. This NWP does not
authorize the removal of sediment and
associated vegetation from natural water
courses except when these activities
have been included in the maintenance
baseline. All dredged material must be
placed in an upland site or an
authorized disposal site in waters of the
United States, and proper siltation
controls must be used.
Maintenance Baseline: The
maintenance baseline is a description of
the physical characteristics (e.g., depth,
width, length, location, configuration, or
design flood capacity, etc.) of a flood
control project within which
maintenance activities are normally
authorized by NWP 31, subject to any
case-specific conditions required by the
district engineer. The district engineer
will approve the maintenance baseline
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based on the approved or constructed
capacity of the flood control facility,
whichever is smaller, including any
areas where there are no constructed
channels, but which are part of the
facility. The prospective permittee will
provide documentation of the physical
characteristics of the flood control
facility (which will normally consist of
as-built or approved drawings) and
documentation of the approved and
constructed design capacities of the
flood control facility. If no evidence of
the constructed capacity exists, the
approved capacity will be used. The
documentation will also include best
management practices to ensure that the
impacts to the aquatic environment are
minimal, especially in maintenance
areas where there are no constructed
channels. (The Corps may request
maintenance records in areas where
there has not been recent maintenance.)
Revocation or modification of the final
determination of the maintenance
baseline can only be done in accordance
with 33 CFR 330.5. Except in
emergencies as described below, this
NWP cannot be used until the district
engineer approves the maintenance
baseline and determines the need for
mitigation and any regional or activityspecific conditions. Once determined,
the maintenance baseline will remain
valid for any subsequent reissuance of
this NWP. This NWP does not authorize
maintenance of a flood control facility
that has been abandoned. A flood
control facility will be considered
abandoned if it has operated at a
significantly reduced capacity without
needed maintenance being
accomplished in a timely manner.
Mitigation: The district engineer will
determine any required mitigation onetime only for impacts associated with
maintenance work at the same time that
the maintenance baseline is approved.
Such one-time mitigation will be
required when necessary to ensure that
adverse environmental impacts are no
more than minimal, both individually
and cumulatively. Such mitigation will
only be required once for any specific
reach of a flood control project.
However, if one-time mitigation is
required for impacts associated with
maintenance activities, the district
engineer will not delay needed
maintenance, provided the district
engineer and the permittee establish a
schedule for identification, approval,
development, construction and
completion of any such required
mitigation. Once the one-time
mitigation described above has been
completed, or a determination made
that mitigation is not required, no
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further mitigation will be required for
maintenance activities within the
maintenance baseline. In determining
appropriate mitigation, the district
engineer will give special consideration
to natural water courses that have been
included in the maintenance baseline
and require compensatory mitigation
and/or best management practices as
appropriate.
Emergency Situations: In emergency
situations, this NWP may be used to
authorize maintenance activities in
flood control facilities for which no
maintenance baseline has been
approved. Emergency situations are
those which would result in an
unacceptable hazard to life, a significant
loss of property, or an immediate,
unforeseen, and significant economic
hardship if action is not taken before a
maintenance baseline can be approved.
In such situations, the determination of
mitigation requirements, if any, may be
deferred until the emergency has been
resolved. Once the emergency has
ended, a maintenance baseline must be
established expeditiously, and
mitigation, including mitigation for
maintenance conducted during the
emergency, must be required as
appropriate.
Notification: The permittee must
submit a pre-construction notification to
the district engineer before any
maintenance work is conducted (see
general condition 27). The preconstruction notification may be for
activity-specific maintenance or for
maintenance of the entire flood control
facility by submitting a five-year (or
less) maintenance plan. The preconstruction notification must include a
description of the maintenance baseline
and the dredged material disposal site.
(Sections 10 and 404)
32. Completed Enforcement Actions.
Any structure, work, or discharge of
dredged or fill material remaining in
place or undertaken for mitigation,
restoration, or environmental benefit in
compliance with either:
(i) The terms of a final written Corps
non-judicial settlement agreement
resolving a violation of Section 404 of
the Clean Water Act and/or Section 10
of the Rivers and Harbors Act of 1899;
or the terms of an EPA 309(a) order on
consent resolving a violation of Section
404 of the Clean Water Act, provided
that:
(a) The unauthorized activity affected
no more than 5 acres of non-tidal waters
or 1 acre of tidal waters;
(b) The settlement agreement provides
for environmental benefits, to an equal
or greater degree, than the
environmental detriments caused by the
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unauthorized activity that is authorized
by this NWP; and
(c) The district engineer issues a
verification letter authorizing the
activity subject to the terms and
conditions of this NWP and the
settlement agreement, including a
specified completion date; or
(ii) The terms of a final Federal court
decision, consent decree, or settlement
agreement resulting from an
enforcement action brought by the
United States under Section 404 of the
Clean Water Act and/or Section 10 of
the Rivers and Harbors Act of 1899; or
(iii) The terms of a final court
decision, consent decree, settlement
agreement, or non-judicial settlement
agreement resulting from a natural
resource damage claim brought by a
trustee or trustees for natural resources
(as defined by the National Contingency
Plan at 40 CFR subpart G) under Section
311 of the Clean Water Act, Section 107
of the Comprehensive Environmental
Response, Compensation and Liability
Act, Section 312 of the National Marine
Sanctuaries Act, Section 1002 of the Oil
Pollution Act of 1990, or the Park
System Resource Protection Act at 16
U.S.C. 19jj, to the extent that a Corps
permit is required.
Compliance is a condition of the NWP
itself. Any authorization under this
NWP is automatically revoked if the
permittee does not comply with the
terms of this NWP or the terms of the
court decision, consent decree, or
judicial/non-judicial settlement
agreement. This NWP does not apply to
any activities occurring after the date of
the decision, decree, or agreement that
are not for the purpose of mitigation,
restoration, or environmental benefit.
Before reaching any settlement
agreement, the Corps will ensure
compliance with the provisions of 33
CFR part 326 and 33 CFR 330.6(d)(2)
and (e). (Sections 10 and 404)
33. Temporary Construction, Access,
and Dewatering. Temporary structures,
work, and discharges, including
cofferdams, necessary for construction
activities or access fills or dewatering of
construction sites, provided that the
associated primary activity is authorized
by the Corps of Engineers or the U.S.
Coast Guard. This NWP also authorizes
temporary structures, work, and
discharges, including cofferdams,
necessary for construction activities not
otherwise subject to the Corps or U.S.
Coast Guard permit requirements.
Appropriate measures must be taken to
maintain near normal downstream flows
and to minimize flooding. Fill must
consist of materials, and be placed in a
manner, that will not be eroded by
expected high flows. The use of dredged
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material may be allowed if the district
engineer determines that it will not
cause more than minimal adverse effects
on aquatic resources. Following
completion of construction, temporary
fill must be entirely removed to upland
areas, dredged material must be
returned to its original location, and the
affected areas must be restored to preconstruction elevations. The affected
areas must also be revegetated, as
appropriate. This permit does not
authorize the use of cofferdams to
dewater wetlands or other aquatic areas
to change their use. Structures left in
place after construction is completed
require a section 10 permit if located in
navigable waters of the United States.
(See 33 CFR part 322.)
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity (see general
condition 27). The pre-construction
notification must include a restoration
plan showing how all temporary fills
and structures will be removed and the
area restored to pre-project conditions.
(Sections 10 and 404)
34. Cranberry Production Activities.
Discharges of dredged or fill material for
dikes, berms, pumps, water control
structures or leveling of cranberry beds
associated with expansion,
enhancement, or modification activities
at existing cranberry production
operations. The cumulative total acreage
of disturbance per cranberry production
operation, including but not limited to,
filling, flooding, ditching, or clearing,
must not exceed 10 acres of waters of
the United States, including wetlands.
The activity must not result in a net loss
of wetland acreage. This NWP does not
authorize any discharge of dredged or
fill material related to other cranberry
production activities such as
warehouses, processing facilities, or
parking areas. For the purposes of this
NWP, the cumulative total of 10 acres
will be measured over the period that
this NWP is valid.
Notification: The permittee must
submit a pre-construction notification to
the district engineer once during the
period that this NWP is valid, and the
NWP will then authorize discharges of
dredge or fill material at an existing
operation for the permit term, provided
the 10-acre limit is not exceeded. (See
general condition 27.) (Section 404)
35. Maintenance Dredging of Existing
Basins. Excavation and removal of
accumulated sediment for maintenance
of existing marina basins, access
channels to marinas or boat slips, and
boat slips to previously authorized
depths or controlling depths for ingress/
egress, whichever is less, provided the
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dredged material is deposited at an
upland site and proper siltation controls
are used. (Section 10)
36. Boat Ramps. Activities required
for the construction of boat ramps,
provided the activity meets all of the
following criteria:
(a) The discharge into waters of the
United States does not exceed 50 cubic
yards of concrete, rock, crushed stone or
gravel into forms, or in the form of precast concrete planks or slabs, unless the
50 cubic yard limit is waived in writing
by the district engineer;
(b) The boat ramp does not exceed 20
feet in width, unless this criterion is
waived in writing by the district
engineer;
(c) The base material is crushed stone,
gravel or other suitable material;
(d) The excavation is limited to the
area necessary for site preparation and
all excavated material is removed to the
upland; and,
(e) No material is placed in special
aquatic sites, including wetlands.
The use of unsuitable material that is
structurally unstable is not authorized.
If dredging in navigable waters of the
United States is necessary to provide
access to the boat ramp, the dredging
may be authorized by another NWP, a
regional general permit, or an individual
permit.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity if: (1) The
discharge into waters of the United
States exceeds 50 cubic yards, or (2) the
boat ramp exceeds 20 feet in width. (See
general condition 27.) (Sections 10 and
404)
37. Emergency Watershed Protection
and Rehabilitation. Work done by or
funded by:
(a) The Natural Resources
Conservation Service for a situation
requiring immediate action under its
emergency Watershed Protection
Program (7 CFR part 624);
(b) The U.S. Forest Service under its
Burned-Area Emergency Rehabilitation
Handbook (FSH 509.13);
(c) The Department of the Interior for
wildland fire management burned area
emergency stabilization and
rehabilitation (DOI Manual part 620, Ch.
3);
(d) The Office of Surface Mining, or
states with approved programs, for
abandoned mine land reclamation
activities under Title IV of the Surface
Mining Control and Reclamation Act (30
CFR subchapter R), where the activity
does not involve coal extraction; or
(e) The Farm Service Agency under its
Emergency Conservation Program (7
CFR part 701).
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In general, the prospective permittee
should wait until the district engineer
issues an NWP verification before
proceeding with the watershed
protection and rehabilitation activity.
However, in cases where there is an
unacceptable hazard to life or a
significant loss of property or economic
hardship will occur, the emergency
watershed protection and rehabilitation
activity may proceed immediately and
the district engineer will consider the
information in the pre-construction
notification any comments received as a
result of agency coordination to decide
whether the NWP 37 authorization
should be modified, suspended, or
revoked in accordance with the
procedures at 33 CFR 330.5.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity (see general
condition 27). (Sections 10 and 404)
38. Cleanup of Hazardous and Toxic
Waste. Specific activities required to
effect the containment, stabilization, or
removal of hazardous or toxic waste
materials that are performed, ordered, or
sponsored by a government agency with
established legal or regulatory authority.
Court ordered remedial action plans or
related settlements are also authorized
by this NWP. This NWP does not
authorize the establishment of new
disposal sites or the expansion of
existing sites used for the disposal of
hazardous or toxic waste.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Sections 10 and 404)
Note: Activities undertaken entirely on a
Comprehensive Environmental Response,
Compensation, and Liability Act (CERCLA)
site by authority of CERCLA as approved or
required by EPA, are not required to obtain
permits under Section 404 of the Clean Water
Act or Section 10 of the Rivers and Harbors
Act.
39. Commercial and Institutional
Developments. Discharges of dredged or
fill material into non-tidal waters of the
United States for the construction or
expansion of commercial and
institutional building foundations and
building pads and attendant features
that are necessary for the use and
maintenance of the structures.
Attendant features may include, but are
not limited to, roads, parking lots,
garages, yards, utility lines, storm water
management facilities, and recreation
facilities such as playgrounds and
playing fields. Examples of commercial
developments include retail stores,
industrial facilities, restaurants,
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business parks, and shopping centers.
Examples of institutional developments
include schools, fire stations,
government office buildings, judicial
buildings, public works buildings,
libraries, hospitals, and places of
worship. The construction of new golf
courses, new ski areas, or oil and gas
wells is not authorized by this NWP.
The discharge must not cause the loss
of greater than 1⁄2-acre of non-tidal
waters of the United States, including
the loss of no more than 300 linear feet
of stream bed, unless for intermittent
and ephemeral stream beds this 300
linear foot limit is waived in writing by
the district engineer. This NWP does not
authorize discharges into non-tidal
wetlands adjacent to tidal waters.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Sections 10 and 404)
40. Agricultural Activities. Discharges
of dredged or fill material into non-tidal
waters of the United States for
agricultural activities, including the
construction of building pads for farm
buildings. Authorized activities include
the installation, placement, or
construction of drainage tiles, ditches,
or levees; mechanized land clearing;
land leveling; the relocation of existing
serviceable drainage ditches constructed
in waters of the United States; and
similar activities.
This NWP also authorizes the
construction of farm ponds in non-tidal
waters of the United States, excluding
perennial streams, provided the farm
pond is used solely for agricultural
purposes. This NWP does not authorize
the construction of aquaculture ponds.
This NWP also authorizes discharges
of dredged or fill material into non-tidal
waters of the United States to relocate
existing serviceable drainage ditches
constructed in non-tidal streams.
The discharge must not cause the loss
of greater than 1⁄2-acre of non-tidal
waters of the United States. This NWP
does not authorize discharges into nontidal wetlands adjacent to tidal waters.
This NWP does not authorize the
relocation of greater than 300 linear feet
of existing serviceable drainage ditches
constructed in non-tidal streams, unless
for drainage ditches constructed in
intermittent and ephemeral streams, this
300 linear foot limit is waived in writing
by the district engineer.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Section 404)
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Note: Some discharges for agricultural
activities may qualify for an exemption under
Section 404(f) of the Clean Water Act (see 33
CFR 323.4). This NWP authorizes the
construction of farm ponds that do not
qualify for the Clean Water Act Section
404(f)(1)(C) exemption because of the
recapture provision at Section 404(f)(2).
41. Reshaping Existing Drainage
Ditches. Discharges of dredged or fill
material into non-tidal waters of the
United States, excluding non-tidal
wetlands adjacent to tidal waters, to
modify the cross-sectional configuration
of currently serviceable drainage ditches
constructed in waters of the United
States, for the purpose of improving
water quality by regrading the drainage
ditch with gentler slopes, which can
reduce erosion, increase growth of
vegetation, and increase uptake of
nutrients and other substances by
vegetation. The reshaping of the ditch
cannot increase drainage capacity
beyond the original as-built capacity nor
can it expand the area drained by the
ditch as originally constructed (i.e., the
capacity of the ditch must be the same
as originally constructed and it cannot
drain additional wetlands or other
waters of the United States).
Compensatory mitigation is not required
because the work is designed to improve
water quality.
This NWP does not authorize the
relocation of drainage ditches
constructed in waters of the United
States; the location of the centerline of
the reshaped drainage ditch must be
approximately the same as the location
of the centerline of the original drainage
ditch. This NWP does not authorize
stream channelization or stream
relocation projects.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity, if more than
500 linear feet of drainage ditch will be
reshaped. (See general condition 27.)
(Section 404)
42. Recreational Facilities. Discharges
of dredged or fill material into non-tidal
waters of the United States for the
construction or expansion of
recreational facilities. Examples of
recreational facilities that may be
authorized by this NWP include playing
fields (e.g., football fields, baseball
fields), basketball courts, tennis courts,
hiking trails, bike paths, golf courses,
ski areas, horse paths, nature centers,
and campgrounds (excluding
recreational vehicle parks). This NWP
also authorizes the construction or
expansion of small support facilities,
such as maintenance and storage
buildings and stables that are directly
related to the recreational activity, but it
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does not authorize the construction of
hotels, restaurants, racetracks, stadiums,
arenas, or similar facilities.
The discharge must not cause the loss
of greater than 1⁄2-acre of non-tidal
waters of the United States, including
the loss of no more than 300 linear feet
of stream bed, unless for intermittent
and ephemeral stream beds this 300
linear foot limit is waived in writing by
the district engineer. This NWP does not
authorize discharges into non-tidal
wetlands adjacent to tidal waters.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Section 404)
43. Stormwater Management
Facilities. Discharges of dredged or fill
material into non-tidal waters of the
United States for the construction and
maintenance of stormwater management
facilities, including the excavation of
stormwater ponds/facilities, detention
basins, and retention basins; the
installation and maintenance of water
control structures, outfall structures and
emergency spillways; and the
maintenance dredging of existing
stormwater management ponds/
facilities and detention and retention
basins.
The discharge must not cause the loss
of greater than 1⁄2-acre of non-tidal
waters of the United States, including
the loss of no more than 300 linear feet
of stream bed, unless for intermittent
and ephemeral stream beds this 300
linear foot limit is waived in writing by
the district engineer. This NWP does not
authorize discharges into non-tidal
wetlands adjacent to tidal waters. This
NWP does not authorize discharges of
dredged or fill material for the
construction of new stormwater
management facilities in perennial
streams.
Notification: For the construction of
new stormwater management facilities,
or the expansion of existing stormwater
management facilities, the permittee
must submit a pre-construction
notification to the district engineer prior
to commencing the activity. (See general
condition 27.) Maintenance activities do
not require pre-construction notification
if they are limited to restoring the
original design capacities of the
stormwater management facility.
(Section 404)
44. Mining Activities. Discharges of
dredged or fill material into non-tidal
waters of the United States for mining
activities, except for coal mining
activities. The discharge must not cause
the loss of greater than 1⁄2-acre of nontidal waters of the United States. This
NWP does not authorize discharges into
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non-tidal wetlands adjacent to tidal
waters.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) If reclamation is required
by other statutes, then a copy of the
reclamation plan must be submitted
with the pre-construction notification.
(Sections 10 and 404)
45. Repair of Uplands Damaged by
Discrete Events. This NWP authorizes
discharges of dredged or fill material,
including dredging or excavation, into
all waters of the United States for
activities associated with the restoration
of upland areas damaged by storms,
floods, or other discrete events. This
NWP authorizes bank stabilization to
protect the restored uplands. The
restoration of the damaged areas,
including any bank stabilization, must
not exceed the contours, or ordinary
high water mark, that existed before the
damage occurred. The district engineer
retains the right to determine the extent
of the pre-existing conditions and the
extent of any restoration work
authorized by this NWP. The work must
commence, or be under contract to
commence, within two years of the date
of damage, unless this condition is
waived in writing by the district
engineer. This NWP cannot be used to
reclaim lands lost to normal erosion
processes over an extended period.
Minor dredging is limited to the
amount necessary to restore the
damaged upland area and should not
significantly alter the pre-existing
bottom contours of the waterbody.
Notification: The permittee must
submit a pre-construction notification to
the district engineer (see general
condition 27) within 12-months of the
date of the damage. The preconstruction notification should include
documentation, such as a recent
topographic survey or photographs, to
justify the extent of the proposed
restoration. (Sections 10 and 404)
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Note: Uplands lost as a result of a storm,
flood, or other discrete event can be replaced
without a section 404 permit, if the uplands
are restored to the ordinary high water mark
(in non-tidal waters) or high tide line (in tidal
waters). (See also 33 CFR 328.5.)
46. Discharges in Ditches. Discharges
of dredged or fill material into non-tidal
ditches that are: (1) Constructed in
uplands, (2) receive water from an area
determined to be a water of the United
States prior to the construction of the
ditch, (3) divert water to an area
determined to be a water of the United
States prior to the construction of the
ditch, and (4) are determined to be
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waters of the United States. The
discharge must not cause the loss of
greater than one acre of waters of the
United States.
This NWP does not authorize
discharges of dredged or fill material
into ditches constructed in streams or
other waters of the United States, or in
streams that have been relocated in
uplands. This NWP does not authorize
discharges of dredged or fill material
that increase the capacity of the ditch
and drain those areas determined to be
waters of the United States prior to
construction of the ditch.
Notification: The permittee must
submit a pre-construction notification to
the district engineer prior to
commencing the activity. (See general
condition 27.) (Section 404)
47. Pipeline Safety Program
Designated Time Sensitive Inspections
and Repairs. Activities required for the
inspection, repair, rehabilitation, or
replacement of any currently serviceable
structure or fill for pipelines that have
been identified by the Pipeline and
Hazardous Materials Safety
Administration’s Pipeline Safety
Program (PHP) within the U.S.
Department of Transportation as timesensitive (see 49 CFR parts 192 and 195)
and additional maintenance activities
done in conjunction with the timesensitive inspection and repair
activities. All activities must meet the
following criteria:
(a) Appropriate measures must be
taken to maintain normal downstream
flows and minimize flooding to the
maximum extent practicable when
temporary structures, work and
discharges, including cofferdams, are
necessary for construction activities or
access fills or dewatering of
construction sites;
(b) Material resulting from trench
excavation may be temporarily sidecast
into waters of the United States for no
more than three months, provided that
the material is not placed in such a
manner that it is dispersed by currents
or other forces. The district engineer
may extend the period of temporary side
casting for no more than a total of 180
days, where appropriate. The trench
cannot be constructed or backfilled in
such a manner as to drain waters of the
United States (e.g., backfilling with
extensive gravel layers, creating a french
drain effect);
(c) Temporary fill must consist of
materials, and be placed in a manner,
that will not be eroded by expected high
flows. Temporary fills must be removed
in their entirety and the affected areas
returned to pre-construction elevations.
The affected areas must be revegetated,
as appropriate;
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(d) In wetlands, the top 6 to 12 inches
of the trench should normally be
backfilled with topsoil from the trench
so that there is no change in
preconstruction contours;
(e) To the maximum extent
practicable, the restoration of open
waters must be to the pre-construction
course, condition, capacity, and location
of the waterbody;
(f) Any exposed slopes and stream
banks must be stabilized immediately
upon completion of the project;
(g) Additional maintenance activities
done in conjunction with the timesensitive inspection or repair must not
result in additional losses of waters of
the United States; and,
(h) The permittee is a participant in
the Pipeline Repair and Environmental
Guidance System (PREGS).
Reporting: The permittee must submit
a post construction report to the PHP
within seven days after completing the
work. The report must be submitted
electronically to PHP via PREGS. The
report must contain the following
information: Project sites located in
waters of the United States, temporary
access routes, stream dewatering sites,
temporary fills and temporary structures
identified on a map of the pipeline
corridor; photographs of the pre- and
post-construction work areas located in
waters of the United States; and a list of
best management practices employed
for each pipeline segment shown on the
map. (Section 10 and 404)
Note: Division engineers may modify this
NWP by adding regional conditions to
protect the aquatic environment, as long as
those regional conditions do not require preconstruction notification or other actions that
would delay time sensitive inspections and
repairs. Examples of appropriate regional
conditions include best management
practices.
48. Existing Commercial Shellfish
Aquaculture Activities. This NWP
authorizes the installation of buoys,
floats, racks, trays, nets, lines, tubes,
containers, and other structures
necessary for the continued operation of
the existing commercial aquaculture
activity. This NWP also authorizes
discharges of dredged or fill material
necessary for shellfish seeding, rearing,
cultivating, transplanting, and
harvesting activities. Rafts and other
floating structures must be securely
anchored and clearly marked.
This NWP does not authorize new
operations or the expansion of the
project area for an existing commercial
shellfish aquaculture activity. This NWP
does not authorize the cultivation of
new species (i.e., species not previously
cultivated in the waterbody). This NWP
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forfeiture contracts. The permittee must
clearly demonstrate to the district
engineer that the reclamation plan will
result in a net increase in aquatic
resource functions. As part of the
project, the permittee may conduct coal
mining activities in an adjacent area,
provided the newly mined area is less
than 40 percent of the area being
remined plus any unmined area
necessary for the reclamation of the
remined area.
Notification: The permittee must
submit a pre-construction notification to
the district engineer and receive written
authorization prior to commencing the
activity. (See general condition 27.)
(Sections 10 and 404)
50. Underground Coal Mining
Activities. Discharges of dredged or fill
material into non-tidal waters of the
United States associated with
underground coal mining and
reclamation operations provided the
activities are authorized, or are
currently being processed as part of an
integrated permit processing procedure,
by the Department of Interior (DOI),
Office of Surface Mining (OSM), or by
states with approved programs under
Title V of the Surface Mining Control
and Reclamation Act of 1977.
This NWP does not authorize
discharges into non-tidal wetlands
adjacent to tidal waters. This NWP does
not authorize coal preparation and
processing activities outside of the mine
site.
Notification: The permittee must
submit a pre-construction notification to
the district engineer and receive written
authorization prior to commencing the
activity. (See general condition 27.) If
reclamation is required by other
statutes, then a copy of the reclamation
plan must be submitted with the preconstruction notification. (Sections 10
and 404)
Note: The permittee should notify the
applicable U.S. Coast Guard office regarding
the project.
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does not authorize attendant features
such as docks, piers, boat ramps,
stockpiles, staging areas, or the
deposition of shell material back into
waters of the United States as waste.
Reporting: For those activities that do
not require pre-construction
notification, the permittee must submit
a report to the district engineer that
includes the following information: (1)
The size of the project area for the
commercial shellfish aquaculture
activity (in acres); (2) the location of the
activity; (3) a brief description of the
culture method and harvesting
method(s); (4) the name(s) of the
cultivated species; and (5) whether
canopy predator nets are being used.
This is a subset of the information that
would be required for pre-construction
notification. This report may be
provided by letter or using an optional
reporting form provided by the Corps.
Only one report needs to be submitted
during the period this NWP is valid, as
long as there are no changes to the
operation that require pre-construction
notification. The report must be
submitted to the district engineer within
90 days of the effective date of this
NWP.
Notification: The permittee must
submit a pre-construction notification to
the district engineer if: (1) The project
area is greater than 100 acres; or (2)
there is any reconfiguration of the
aquaculture activity, such as relocating
existing operations into portions of the
project area not previously used for
aquaculture activities; or (3) there is a
change in species being cultivated; or
(4) there is a change in culture methods
(e.g., from bottom culture to off-bottom
culture); or (5) dredge harvesting, tilling,
or harrowing is conducted in areas
inhabited by submerged aquatic
vegetation. (See general condition 27.)
(Sections 10 and 404)
Note: Coal preparation and processing
activities outside of the mine site may be
authorized by NWP 21.
49. Coal Remining Activities.
Discharges of dredged or fill material
into non-tidal waters of the United
States associated with the remining and
reclamation of lands that were
previously mined for coal, provided the
activities are already authorized, or are
currently being processed as part of an
integrated permit processing procedure,
by the Department of Interior (DOI)
Office of Surface Mining (OSM), or by
states with approved programs under
Title IV or Title V of the Surface Mining
Control and Reclamation Act of 1977.
Areas previously mined include
reclaimed mine sites, abandoned mine
land areas, or lands under bond
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C. Nationwide Permit General
Conditions
Note: To qualify for NWP authorization,
the prospective permittee must comply with
the following general conditions, as
appropriate, in addition to any regional or
case-specific conditions imposed by the
division engineer or district engineer.
Prospective permittees should contact the
appropriate Corps district office to determine
if regional conditions have been imposed on
an NWP. Prospective permittees should also
contact the appropriate Corps district office
to determine the status of Clean Water Act
Section 401 water quality certification and/
or Coastal Zone Management Act consistency
for an NWP.
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1. Navigation. (a) No activity may
cause more than a minimal adverse
effect on navigation.
(b) Any safety lights and signals
prescribed by the U.S. Coast Guard,
through regulations or otherwise, must
be installed and maintained at the
permittee’s expense on authorized
facilities in navigable waters of the
United States.
(c) The permittee understands and
agrees that, if future operations by the
United States require the removal,
relocation, or other alteration, of the
structure or work herein authorized, or
if, in the opinion of the Secretary of the
Army or his authorized representative,
said structure or work shall cause
unreasonable obstruction to the free
navigation of the navigable waters, the
permittee will be required, upon due
notice from the Corps of Engineers, to
remove, relocate, or alter the structural
work or obstructions caused thereby,
without expense to the United States.
No claim shall be made against the
United States on account of any such
removal or alteration.
2. Aquatic Life Movements. No
activity may substantially disrupt the
necessary life cycle movements of those
species of aquatic life indigenous to the
waterbody, including those species that
normally migrate through the area,
unless the activity’s primary purpose is
to impound water. Culverts placed in
streams must be installed to maintain
low flow conditions.
3. Spawning Areas. Activities in
spawning areas during spawning
seasons must be avoided to the
maximum extent practicable. Activities
that result in the physical destruction
(e.g., through excavation, fill, or
downstream smothering by substantial
turbidity) of an important spawning area
are not authorized.
4. Migratory Bird Breeding Areas.
Activities in waters of the United States
that serve as breeding areas for
migratory birds must be avoided to the
maximum extent practicable.
5. Shellfish Beds. No activity may
occur in areas of concentrated shellfish
populations, unless the activity is
directly related to a shellfish harvesting
activity authorized by NWPs 4 and 48.
6. Suitable Material. No activity may
use unsuitable material (e.g., trash,
debris, car bodies, asphalt, etc.).
Material used for construction or
discharged must be free from toxic
pollutants in toxic amounts (see Section
307 of the Clean Water Act).
7. Water Supply Intakes. No activity
may occur in the proximity of a public
water supply intake, except where the
activity is for the repair or improvement
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of public water supply intake structures
or adjacent bank stabilization.
8. Adverse Effects From
Impoundments. If the activity creates an
impoundment of water, adverse effects
to the aquatic system due to accelerating
the passage of water, and/or restricting
its flow must be minimized to the
maximum extent practicable.
9. Management of Water Flows. To the
maximum extent practicable, the preconstruction course, condition,
capacity, and location of open waters
must be maintained for each activity,
including stream channelization and
storm water management activities,
except as provided below. The activity
must be constructed to withstand
expected high flows. The activity must
not restrict or impede the passage of
normal or high flows, unless the
primary purpose of the activity is to
impound water or manage high flows.
The activity may alter the preconstruction course, condition,
capacity, and location of open waters if
it benefits the aquatic environment (e.g.,
stream restoration or relocation
activities).
10. Fills Within 100-Year Floodplains.
The activity must comply with
applicable FEMA-approved state or
local floodplain management
requirements.
11. Equipment. Heavy equipment
working in wetlands or mudflats must
be placed on mats, or other measures
must be taken to minimize soil
disturbance.
12. Soil Erosion and Sediment
Controls. Appropriate soil erosion and
sediment controls must be used and
maintained in effective operating
condition during construction, and all
exposed soil and other fills, as well as
any work below the ordinary high water
mark or high tide line, must be
permanently stabilized at the earliest
practicable date. Permittees are
encouraged to perform work within
waters of the United States during
periods of low-flow or no-flow.
13. Removal of Temporary Fills.
Temporary fills must be removed in
their entirety and the affected areas
returned to pre-construction elevations.
The affected areas must be revegetated,
as appropriate.
14. Proper Maintenance. Any
authorized structure or fill shall be
properly maintained, including
maintenance to ensure public safety.
15. Wild and Scenic Rivers. No
activity may occur in a component of
the National Wild and Scenic River
System, or in a river officially
designated by Congress as a ‘‘study
river’’ for possible inclusion in the
system while the river is in an official
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study status, unless the appropriate
Federal agency with direct management
responsibility for such river, has
determined in writing that the proposed
activity will not adversely affect the
Wild and Scenic River designation or
study status. Information on Wild and
Scenic Rivers may be obtained from the
appropriate Federal land management
agency in the area (e.g., National Park
Service, U.S. Forest Service, Bureau of
Land Management, U.S. Fish and
Wildlife Service).
16. Tribal Rights. No activity or its
operation may impair reserved tribal
rights, including, but not limited to,
reserved water rights and treaty fishing
and hunting rights.
17. Endangered Species. (a) No
activity is authorized under any NWP
which is likely to jeopardize the
continued existence of a threatened or
endangered species or a species
proposed for such designation, as
identified under the Federal Endangered
Species Act (ESA), or which will
destroy or adversely modify the critical
habitat of such species. No activity is
authorized under any NWP which ‘‘may
affect’’ a listed species or critical
habitat, unless Section 7 consultation
addressing the effects of the proposed
activity has been completed.
(b) Federal agencies should follow
their own procedures for complying
with the requirements of the ESA.
Federal permittees must provide the
district engineer with the appropriate
documentation to demonstrate
compliance with those requirements.
(c) Non-federal permittees shall notify
the district engineer if any listed species
or designated critical habitat might be
affected or is in the vicinity of the
project, or if the project is located in
designated critical habitat, and shall not
begin work on the activity until notified
by the district engineer that the
requirements of the ESA have been
satisfied and that the activity is
authorized. For activities that might
affect Federally-listed endangered or
threatened species or designated critical
habitat, the pre-construction notification
must include the name(s) of the
endangered or threatened species that
may be affected by the proposed work
or that utilize the designated critical
habitat that may be affected by the
proposed work. The district engineer
will determine whether the proposed
activity ‘‘may affect’’ or will have ‘‘no
effect’’ to listed species and designated
critical habitat and will notify the nonFederal applicant of the Corps’
determination within 45 days of receipt
of a complete pre-construction
notification. In cases where the nonFederal applicant has identified listed
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species or critical habitat that might be
affected or is in the vicinity of the
project, and has so notified the Corps,
the applicant shall not begin work until
the Corps has provided notification the
proposed activities will have ‘‘no effect’’
on listed species or critical habitat, or
until Section 7 consultation has been
completed.
(d) As a result of formal or informal
consultation with the FWS or NMFS the
district engineer may add speciesspecific regional endangered species
conditions to the NWPs.
(e) Authorization of an activity by a
NWP does not authorize the ‘‘take’’ of a
threatened or endangered species as
defined under the ESA. In the absence
of separate authorization (e.g., an ESA
Section 10 Permit, a Biological Opinion
with ‘‘incidental take’’ provisions, etc.)
from the U.S. FWS or the NMFS, both
lethal and non-lethal ‘‘takes’’ of
protected species are in violation of the
ESA. Information on the location of
threatened and endangered species and
their critical habitat can be obtained
directly from the offices of the U.S. FWS
and NMFS or their world wide Web
pages at https://www.fws.gov/ and
https://www.noaa.gov/fisheries.html
respectively.
18. Historic Properties. (a) In cases
where the district engineer determines
that the activity may affect properties
listed, or eligible for listing, in the
National Register of Historic Places, the
activity is not authorized, until the
requirements of Section 106 of the
National Historic Preservation Act
(NHPA) have been satisfied.
(b) Federal permittees should follow
their own procedures for complying
with the requirements of Section 106 of
the National Historic Preservation Act.
Federal permittees must provide the
district engineer with the appropriate
documentation to demonstrate
compliance with those requirements.
(c) Non-federal permittees must
submit a pre-construction notification to
the district engineer if the authorized
activity may have the potential to cause
effects to any historic properties listed,
determined to be eligible for listing on,
or potentially eligible for listing on the
National Register of Historic Places,
including previously unidentified
properties. For such activities, the preconstruction notification must state
which historic properties may be
affected by the proposed work or
include a vicinity map indicating the
location of the historic properties or the
potential for the presence of historic
properties. Assistance regarding
information on the location of or
potential for the presence of historic
resources can be sought from the State
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Historic Preservation Officer or Tribal
Historic Preservation Officer, as
appropriate, and the National Register of
Historic Places (see 33 CFR 330.4(g)).
The district engineer shall make a
reasonable and good faith effort to carry
out appropriate identification efforts,
which may include background
research, consultation, oral history
interviews, sample field investigation,
and field survey. Based on the
information submitted and these efforts,
the district engineer shall determine
whether the proposed activity has the
potential to cause an effect on the
historic properties. Where the nonFederal applicant has identified historic
properties which the activity may have
the potential to cause effects and so
notified the Corps, the non-Federal
applicant shall not begin the activity
until notified by the district engineer
either that the activity has no potential
to cause effects or that consultation
under Section 106 of the NHPA has
been completed.
(d) The district engineer will notify
the prospective permittee within 45
days of receipt of a complete preconstruction notification whether NHPA
Section 106 consultation is required.
Section 106 consultation is not required
when the Corps determines that the
activity does not have the potential to
cause effects on historic properties (see
36 CFR 800.3(a)). If NHPA section 106
consultation is required and will occur,
the district engineer will notify the nonFederal applicant that he or she cannot
begin work until Section 106
consultation is completed.
(e) Prospective permittees should be
aware that section 110k of the NHPA (16
U.S.C. 470h–2(k)) prevents the Corps
from granting a permit or other
assistance to an applicant who, with
intent to avoid the requirements of
Section 106 of the NHPA, has
intentionally significantly adversely
affected a historic property to which the
permit would relate, or having legal
power to prevent it, allowed such
significant adverse effect to occur,
unless the Corps, after consultation with
the Advisory Council on Historic
Preservation (ACHP), determines that
circumstances justify granting such
assistance despite the adverse effect
created or permitted by the applicant. If
circumstances justify granting the
assistance, the Corps is required to
notify the ACHP and provide
documentation specifying the
circumstances, explaining the degree of
damage to the integrity of any historic
properties affected, and proposed
mitigation. This documentation must
include any views obtained from the
applicant, SHPO/THPO, appropriate
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Indian tribes if the undertaking occurs
on or affects historic properties on tribal
lands or affects properties of interest to
those tribes, and other parties known to
have a legitimate interest in the impacts
to the permitted activity on historic
properties.
19. Designated Critical Resource
Waters. Critical resource waters include,
NOAA-designated marine sanctuaries,
National Estuarine Research Reserves,
state natural heritage sites, and
outstanding national resource waters or
other waters officially designated by a
state as having particular environmental
or ecological significance and identified
by the district engineer after notice and
opportunity for public comment. The
district engineer may also designate
additional critical resource waters after
notice and opportunity for comment.
(a) Discharges of dredged or fill
material into waters of the United States
are not authorized by NWPs 7, 12, 14,
16, 17, 21, 29, 31, 35, 39, 40, 42, 43, 44,
49, and 50 for any activity within, or
directly affecting, critical resource
waters, including wetlands adjacent to
such waters.
(b) For NWPs 3, 8, 10, 13, 15, 18, 19,
22, 23, 25, 27, 28, 30, 33, 34, 36, 37, and
38, notification is required in
accordance with general condition 27,
for any activity proposed in the
designated critical resource waters
including wetlands adjacent to those
waters. The district engineer may
authorize activities under these NWPs
only after it is determined that the
impacts to the critical resource waters
will be no more than minimal.
20. Mitigation. The district engineer
will consider the following factors when
determining appropriate and practicable
mitigation necessary to ensure that
adverse effects on the aquatic
environment are minimal:
(a) The activity must be designed and
constructed to avoid and minimize
adverse effects, both temporary and
permanent, to waters of the United
States to the maximum extent
practicable at the project site (i.e., on
site).
(b) Mitigation in all its forms
(avoiding, minimizing, rectifying,
reducing, or compensating) will be
required to the extent necessary to
ensure that the adverse effects to the
aquatic environment are minimal.
(c) Compensatory mitigation at a
minimum one-for-one ratio will be
required for all wetland losses that
exceed 1⁄10 acre and require preconstruction notification, unless the
district engineer determines in writing
that some other form of mitigation
would be more environmentally
appropriate and provides a project-
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11193
specific waiver of this requirement. For
wetland losses of 1⁄10 acre or less that
require pre-construction notification,
the district engineer may determine on
a case-by-case basis that compensatory
mitigation is required to ensure that the
activity results in minimal adverse
effects on the aquatic environment.
Since the likelihood of success is greater
and the impacts to potentially valuable
uplands are reduced, wetland
restoration should be the first
compensatory mitigation option
considered.
(d) For losses of streams or other open
waters that require pre-construction
notification, the district engineer may
require compensatory mitigation, such
as stream restoration, to ensure that the
activity results in minimal adverse
effects on the aquatic environment.
(e) Compensatory mitigation will not
be used to increase the acreage losses
allowed by the acreage limits of the
NWPs. For example, if an NWP has an
acreage limit of 1⁄2 acre, it cannot be
used to authorize any project resulting
in the loss of greater than 1⁄2 acre of
waters of the United States, even if
compensatory mitigation is provided
that replaces or restores some of the lost
waters. However, compensatory
mitigation can and should be used, as
necessary, to ensure that a project
already meeting the established acreage
limits also satisfies the minimal impact
requirement associated with the NWPs.
(f) Compensatory mitigation plans for
projects in or near streams or other open
waters will normally include a
requirement for the establishment,
maintenance, and legal protection (e.g.,
conservation easements) of riparian
areas next to open waters. In some
cases, riparian areas may be the only
compensatory mitigation required.
Riparian areas should consist of native
species. The width of the required
riparian area will address documented
water quality or aquatic habitat loss
concerns. Normally, the riparian area
will be 25 to 50 feet wide on each side
of the stream, but the district engineer
may require slightly wider riparian
areas to address documented water
quality or habitat loss concerns. Where
both wetlands and open waters exist on
the project site, the district engineer will
determine the appropriate
compensatory mitigation (e.g., riparian
areas and/or wetlands compensation)
based on what is best for the aquatic
environment on a watershed basis. In
cases where riparian areas are
determined to be the most appropriate
form of compensatory mitigation, the
district engineer may waive or reduce
the requirement to provide wetland
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compensatory mitigation for wetland
losses.
(g) Permittees may propose the use of
mitigation banks, in-lieu fee
arrangements or separate activityspecific compensatory mitigation. In all
cases, the mitigation provisions will
specify the party responsible for
accomplishing and/or complying with
the mitigation plan.
(h) Where certain functions and
services of waters of the United States
are permanently adversely affected,
such as the conversion of a forested or
scrub-shrub wetland to a herbaceous
wetland in a permanently maintained
utility line right-of-way, mitigation may
be required to reduce the adverse effects
of the project to the minimal level.
21. Water Quality. Where States and
authorized Tribes, or EPA where
applicable, have not previously certified
compliance of an NWP with CWA
Section 401, individual 401 Water
Quality Certification must be obtained
or waived (see 33 CFR 330.4(c)). The
district engineer or State or Tribe may
require additional water quality
management measures to ensure that the
authorized activity does not result in
more than minimal degradation of water
quality.
22. Coastal Zone Management. In
coastal states where an NWP has not
previously received a state coastal zone
management consistency concurrence,
an individual state coastal zone
management consistency concurrence
must be obtained, or a presumption of
concurrence must occur (see 33 CFR
330.4(d)). The district engineer or a
State may require additional measures
to ensure that the authorized activity is
consistent with state coastal zone
management requirements.
23. Regional and Case-By-Case
Conditions. The activity must comply
with any regional conditions that may
have been added by the Division
Engineer (see 33 CFR 330.4(e)) and with
any case specific conditions added by
the Corps or by the state, Indian Tribe,
or U.S. EPA in its section 401 Water
Quality Certification, or by the state in
its Coastal Zone Management Act
consistency determination.
24. Use of Multiple Nationwide
Permits. The use of more than one NWP
for a single and complete project is
prohibited, except when the acreage loss
of waters of the United States
authorized by the NWPs does not
exceed the acreage limit of the NWP
with the highest specified acreage limit.
For example, if a road crossing over
tidal waters is constructed under NWP
14, with associated bank stabilization
authorized by NWP 13, the maximum
acreage loss of waters of the United
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States for the total project cannot exceed
⁄ -acre.
25. Transfer of Nationwide Permit
Verifications. If the permittee sells the
property associated with a nationwide
permit verification, the permittee may
transfer the nationwide permit
verification to the new owner by
submitting a letter to the appropriate
Corps district office to validate the
transfer. A copy of the nationwide
permit verification must be attached to
the letter, and the letter must contain
the following statement and signature:
‘‘When the structures or work
authorized by this nationwide permit
are still in existence at the time the
property is transferred, the terms and
conditions of this nationwide permit,
including any special conditions, will
continue to be binding on the new
owner(s) of the property. To validate the
transfer of this nationwide permit and
the associated liabilities associated with
compliance with its terms and
conditions, have the transferee sign and
date below.’’
llllllllllllllllll
l
(Transferee)
llllllllllllllllll
l
(Date)
26. Compliance Certification. Each
permittee who received an NWP
verification from the Corps must submit
a signed certification regarding the
completed work and any required
mitigation. The certification form must
be forwarded by the Corps with the
NWP verification letter and will
include:
(a) A statement that the authorized
work was done in accordance with the
NWP authorization, including any
general or specific conditions;
(b) A statement that any required
mitigation was completed in accordance
with the permit conditions; and
(c) The signature of the permittee
certifying the completion of the work
and mitigation.
27. Pre-Construction Notification. (a)
Timing. Where required by the terms of
the NWP, the prospective permittee
must notify the district engineer by
submitting a pre-construction
notification (PCN) as early as possible.
The district engineer must determine if
the PCN is complete within 30 calendar
days of the date of receipt and, as a
general rule, will request additional
information necessary to make the PCN
complete only once. However, if the
prospective permittee does not provide
all of the requested information, then
the district engineer will notify the
prospective permittee that the PCN is
still incomplete and the PCN review
13
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process will not commence until all of
the requested information has been
received by the district engineer. The
prospective permittee shall not begin
the activity:
(1) Until notified in writing by the
district engineer that the activity may
proceed under the NWP with any
special conditions imposed by the
district or division engineer; or
(2) If 45 calendar days have passed
from the district engineer’s receipt of
the complete PCN and the prospective
permittee has not received written
notice from the district or division
engineer. However, if the permittee was
required to notify the Corps pursuant to
general condition 17 that listed species
or critical habitat might be affected or in
the vicinity of the project, or to notify
the Corps pursuant to general condition
18 that the activity may have the
potential to cause effects to historic
properties, the permittee cannot begin
the activity until receiving written
notification from the Corps that is ‘‘no
effect’’ on listed species or ‘‘no potential
to cause effects’’ on historic properties,
or that any consultation required under
Section 7 of the Endangered Species Act
(see 33 CFR 330.4(f)) and/or Section 106
of the National Historic Preservation
(see 33 CFR 330.4(g)) is completed.
Also, work cannot begin under NWPs
21, 49, or 50 until the permittee has
received written approval from the
Corps. If the proposed activity requires
a written waiver to exceed specified
limits of an NWP, the permittee cannot
begin the activity until the district
engineer issues the waiver. If the district
or division engineer notifies the
permittee in writing that an individual
permit is required within 45 calendar
days of receipt of a complete PCN, the
permittee cannot begin the activity until
an individual permit has been obtained.
Subsequently, the permittee’s right to
proceed under the NWP may be
modified, suspended, or revoked only in
accordance with the procedure set forth
in 33 CFR 330.5(d)(2).
(b) Contents of Pre-Construction
Notification: The PCN must be in
writing and include the following
information:
(1) Name, address and telephone
numbers of the prospective permittee;
(2) Location of the proposed project;
(3) A description of the proposed
project; the project’s purpose; direct and
indirect adverse environmental effects
the project would cause; any other
NWP(s), regional general permit(s), or
individual permit(s) used or intended to
be used to authorize any part of the
proposed project or any related activity.
The description should be sufficiently
detailed to allow the district engineer to
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determine that the adverse effects of the
project will be minimal and to
determine the need for compensatory
mitigation. Sketches should be provided
when necessary to show that the activity
complies with the terms of the NWP.
(Sketches usually clarify the project and
when provided result in a quicker
decision.);
(4) The PCN must include a
delineation of special aquatic sites and
other waters of the United States on the
project site. Wetland delineations must
be prepared in accordance with the
current method required by the Corps.
The permittee may ask the Corps to
delineate the special aquatic sites and
other waters of the United States, but
there may be a delay if the Corps does
the delineation, especially if the project
site is large or contains many waters of
the United States. Furthermore, the 45
day period will not start until the
delineation has been submitted to or
completed by the Corps, where
appropriate;
(5) If the proposed activity will result
in the loss of greater than 1⁄10 acre of
wetlands and a PCN is required, the
prospective permittee must submit a
statement describing how the mitigation
requirement will be satisfied. As an
alternative, the prospective permittee
may submit a conceptual or detailed
mitigation plan.
(6) If any listed species or designated
critical habitat might be affected or is in
the vicinity of the project, or if the
project is located in designated critical
habitat, for non-Federal applicants the
PCN must include the name(s) of those
endangered or threatened species that
might be affected by the proposed work
or utilize the designated critical habitat
that may be affected by the proposed
work. Federal applicants must provide
documentation demonstrating
compliance with the Endangered
Species Act; and
(7) For an activity that may affect a
historic property listed on, determined
to be eligible for listing on, or
potentially eligible for listing on, the
National Register of Historic Places, for
non-Federal applicants the PCN must
state which historic property may be
affected by the proposed work or
include a vicinity map indicating the
location of the historic property. Federal
applicants must provide documentation
demonstrating compliance with Section
106 of the National Historic
Preservation Act.
(c) Form of Pre-Construction
Notification: The standard individual
permit application form (Form ENG
4345) may be used, but the completed
application form must clearly indicate
that it is a PCN and must include all of
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the information required in paragraphs
(b)(1) through (7) of this general
condition. A letter containing the
required information may also be used.
(d) Agency Coordination: (1) The
district engineer will consider any
comments from Federal and state
agencies concerning the proposed
activity’s compliance with the terms
and conditions of the NWPs and the
need for mitigation to reduce the
project’s adverse environmental effects
to a minimal level.
(2) For all NWP 48 activities requiring
pre-construction notification and for
other NWP activities requiring preconstruction notification to the district
engineer that result in the loss of greater
than 1⁄2-acre of waters of the United
States, the district engineer will
immediately provide (e.g., via facsimile
transmission, overnight mail, or other
expeditious manner) a copy of the PCN
to the appropriate Federal or state
offices (U.S. FWS, state natural resource
or water quality agency, EPA, State
Historic Preservation Officer (SHPO) or
Tribal Historic Preservation Office
(THPO), and, if appropriate, the NMFS).
With the exception of NWP 37, these
agencies will then have 10 calendar
days from the date the material is
transmitted to telephone or fax the
district engineer notice that they intend
to provide substantive, site-specific
comments. If so contacted by an agency,
the district engineer will wait an
additional 15 calendar days before
making a decision on the preconstruction notification. The district
engineer will fully consider agency
comments received within the specified
time frame, but will provide no
response to the resource agency, except
as provided below. The district engineer
will indicate in the administrative
record associated with each preconstruction notification that the
resource agencies’ concerns were
considered. For NWP 37, the emergency
watershed protection and rehabilitation
activity may proceed immediately in
cases where there is an unacceptable
hazard to life or a significant loss of
property or economic hardship will
occur. The district engineer will
consider any comments received to
decide whether the NWP 37
authorization should be modified,
suspended, or revoked in accordance
with the procedures at 33 CFR 330.5.
(3) In cases of where the prospective
permittee is not a Federal agency, the
district engineer will provide a response
to NMFS within 30 calendar days of
receipt of any Essential Fish Habitat
conservation recommendations, as
required by Section 305(b)(4)(B) of the
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Magnuson-Stevens Fishery
Conservation and Management Act.
(4) Applicants are encouraged to
provide the Corps multiple copies of
pre-construction notifications to
expedite agency coordination.
(5) For NWP 48 activities that require
reporting, the district engineer will
provide a copy of each report within 10
calendar days of receipt to the
appropriate regional office of the NMFS.
(e) District Engineer’s Decision: In
reviewing the PCN for the proposed
activity, the district engineer will
determine whether the activity
authorized by the NWP will result in
more than minimal individual or
cumulative adverse environmental
effects or may be contrary to the public
interest. If the proposed activity requires
a PCN and will result in a loss of greater
than 1⁄10 acre of wetlands, the
prospective permittee should submit a
mitigation proposal with the PCN.
Applicants may also propose
compensatory mitigation for projects
with smaller impacts. The district
engineer will consider any proposed
compensatory mitigation the applicant
has included in the proposal in
determining whether the net adverse
environmental effects to the aquatic
environment of the proposed work are
minimal. The compensatory mitigation
proposal may be either conceptual or
detailed. If the district engineer
determines that the activity complies
with the terms and conditions of the
NWP and that the adverse effects on the
aquatic environment are minimal, after
considering mitigation, the district
engineer will notify the permittee and
include any conditions the district
engineer deems necessary. The district
engineer must approve any
compensatory mitigation proposal
before the permittee commences work.
If the prospective permittee elects to
submit a compensatory mitigation plan
with the PCN, the district engineer will
expeditiously review the proposed
compensatory mitigation plan. The
district engineer must review the plan
within 45 calendar days of receiving a
complete PCN and determine whether
the proposed mitigation would ensure
no more than minimal adverse effects
on the aquatic environment. If the net
adverse effects of the project on the
aquatic environment (after
consideration of the compensatory
mitigation proposal) are determined by
the district engineer to be minimal, the
district engineer will provide a timely
written response to the applicant. The
response will state that the project can
proceed under the terms and conditions
of the NWP.
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If the district engineer determines that
the adverse effects of the proposed work
are more than minimal, then the district
engineer will notify the applicant either:
(1) That the project does not qualify for
authorization under the NWP and
instruct the applicant on the procedures
to seek authorization under an
individual permit; (2) that the project is
authorized under the NWP subject to
the applicant’s submission of a
mitigation plan that would reduce the
adverse effects on the aquatic
environment to the minimal level; or (3)
that the project is authorized under the
NWP with specific modifications or
conditions. Where the district engineer
determines that mitigation is required to
ensure no more than minimal adverse
effects occur to the aquatic
environment, the activity will be
authorized within the 45-day PCN
period. The authorization will include
the necessary conceptual or specific
mitigation or a requirement that the
applicant submit a mitigation plan that
would reduce the adverse effects on the
aquatic environment to the minimal
level. When mitigation is required, no
work in waters of the United States may
occur until the district engineer has
approved a specific mitigation plan.
28. Single and Complete Project. The
activity must be a single and complete
project. The same NWP cannot be used
more than once for the same single and
complete project.
D. Further Information
1. District Engineers have authority to
determine if an activity complies with
the terms and conditions of an NWP.
2. NWPs do not obviate the need to
obtain other federal, state, or local
permits, approvals, or authorizations
required by law.
3. NWPs do not grant any property
rights or exclusive privileges.
4. NWPs do not authorize any injury
to the property or rights of others.
5. NWPs do not authorize interference
with any existing or proposed Federal
project.
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E. Definitions
Best management practices (BMPs):
Policies, practices, procedures, or
structures implemented to mitigate the
adverse environmental effects on
surface water quality resulting from
development. BMPs are categorized as
structural or non-structural.
Compensatory mitigation: The
restoration, establishment (creation),
enhancement, or preservation of aquatic
resources for the purpose of
compensating for unavoidable adverse
impacts which remain after all
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appropriate and practicable avoidance
and minimization has been achieved.
Currently serviceable: Useable as is or
with some maintenance, but not so
degraded as to essentially require
reconstruction.
Discharge: The term ‘‘discharge’’
means any discharge of dredged or fill
material and any activity that causes or
results in such a discharge.
Enhancement: The manipulation of
the physical, chemical, or biological
characteristics of an aquatic resource to
heighten, intensify, or improve a
specific aquatic resource function(s).
Enhancement results in the gain of
selected aquatic resource function(s),
but may also lead to a decline in other
aquatic resource function(s).
Enhancement does not result in a gain
in aquatic resource area.
Ephemeral stream: An ephemeral
stream has flowing water only during,
and for a short duration after,
precipitation events in a typical year.
Ephemeral stream beds are located
above the water table year-round.
Groundwater is not a source of water for
the stream. Runoff from rainfall is the
primary source of water for stream flow.
Establishment (creation): The
manipulation of the physical, chemical,
or biological characteristics present to
develop an aquatic resource that did not
previously exist at an upland site.
Establishment results in a gain in
aquatic resource area.
Historic Property: Any prehistoric or
historic district, site (including
archaeological site), building, structure,
or other object included in, or eligible
for inclusion in, the National Register of
Historic Places maintained by the
Secretary of the Interior. This term
includes artifacts, records, and remains
that are related to and located within
such properties. The term includes
properties of traditional religious and
cultural importance to an Indian tribe or
Native Hawaiian organization and that
meet the National Register criteria (36
CFR part 60).
Independent utility: A test to
determine what constitutes a single and
complete project in the Corps regulatory
program. A project is considered to have
independent utility if it would be
constructed absent the construction of
other projects in the project area.
Portions of a multi-phase project that
depend upon other phases of the project
do not have independent utility. Phases
of a project that would be constructed
even if the other phases were not built
can be considered as separate single and
complete projects with independent
utility.
Intermittent stream: An intermittent
stream has flowing water during certain
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times of the year, when groundwater
provides water for stream flow. During
dry periods, intermittent streams may
not have flowing water. Runoff from
rainfall is a supplemental source of
water for stream flow.
Loss of waters of the United States:
Waters of the United States that are
permanently adversely affected by
filling, flooding, excavation, or drainage
because of the regulated activity.
Permanent adverse effects include
permanent discharges of dredged or fill
material that change an aquatic area to
dry land, increase the bottom elevation
of a waterbody, or change the use of a
waterbody. The acreage of loss of waters
of the United States is a threshold
measurement of the impact to
jurisdictional waters for determining
whether a project may qualify for an
NWP; it is not a net threshold that is
calculated after considering
compensatory mitigation that may be
used to offset losses of aquatic functions
and services. The loss of stream bed
includes the linear feet of stream bed
that is filled or excavated. Waters of the
United States temporarily filled,
flooded, excavated, or drained, but
restored to pre-construction contours
and elevations after construction, are
not included in the measurement of loss
of waters of the United States. Impacts
resulting from activities eligible for
exemptions under Section 404(f) of the
Clean Water Act are not considered
when calculating the loss of waters of
the United States.
Non-tidal wetland: A non-tidal
wetland is a wetland that is not subject
to the ebb and flow of tidal waters. The
definition of a wetland can be found at
33 CFR 328.3(b). Non-tidal wetlands
contiguous to tidal waters are located
landward of the high tide line (i.e.,
spring high tide line).
Open water: For purposes of the
NWPs, an open water is any area that in
a year with normal patterns of
precipitation has water flowing or
standing above ground to the extent that
an ordinary high water mark can be
determined. Aquatic vegetation within
the area of standing or flowing water is
either non-emergent, sparse, or absent.
Vegetated shallows are considered to be
open waters. Examples of ‘‘open waters’’
include rivers, streams, lakes, and
ponds.
Ordinary High Water Mark: An
ordinary high water mark is a line on
the shore established by the fluctuations
of water and indicated by physical
characteristics, or by other appropriate
means that consider the characteristics
of the surrounding areas (see 33 CFR
328.3(e)).
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Perennial stream: A perennial stream
has flowing water year-round during a
typical year. The water table is located
above the stream bed for most of the
year. Groundwater is the primary source
of water for stream flow. Runoff from
rainfall is a supplemental source of
water for stream flow.
Practicable: Available and capable of
being done after taking into
consideration cost, existing technology,
and logistics in light of overall project
purposes.
Pre-construction notification: A
request submitted by the project
proponent to the Corps for confirmation
that a particular activity is authorized
by nationwide permit. The request may
be a permit application, letter, or similar
document that includes information
about the proposed work and its
anticipated environmental effects. Preconstruction notification may be
required by the terms and conditions of
a nationwide permit, or by regional
conditions. A pre-construction
notification may be voluntarily
submitted in cases where preconstruction notification is not required
and the project proponent wants
confirmation that the activity is
authorized by nationwide permit.
Preservation: The removal of a threat
to, or preventing the decline of, aquatic
resources by an action in or near those
aquatic resources. This term includes
activities commonly associated with the
protection and maintenance of aquatic
resources through the implementation
of appropriate legal and physical
mechanisms. Preservation does not
result in a gain of aquatic resource area
or functions.
Re-establishment: The manipulation
of the physical, chemical, or biological
characteristics of a site with the goal of
returning natural/historic functions to a
former aquatic resource. Reestablishment results in rebuilding a
former aquatic resource and results in a
gain in aquatic resource area.
Rehabilitation: The manipulation of
the physical, chemical, or biological
characteristics of a site with the goal of
repairing natural/historic functions to a
degraded aquatic resource.
Rehabilitation results in a gain in
aquatic resource function, but does not
result in a gain in aquatic resource area.
Restoration: The manipulation of the
physical, chemical, or biological
characteristics of a site with the goal of
returning natural/historic functions to a
former or degraded aquatic resource. For
the purpose of tracking net gains in
aquatic resource area, restoration is
divided into two categories: Reestablishment and rehabilitation.
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Riffle and pool complex: Riffle and
pool complexes are special aquatic sites
under the 404(b)(1) Guidelines. Riffle
and pool complexes sometimes
characterize steep gradient sections of
streams. Such stream sections are
recognizable by their hydraulic
characteristics. The rapid movement of
water over a course substrate in riffles
results in a rough flow, a turbulent
surface, and high dissolved oxygen
levels in the water. Pools are deeper
areas associated with riffles. A slower
stream velocity, a streaming flow, a
smooth surface, and a finer substrate
characterize pools.
Riparian areas: Riparian areas are
lands adjacent to streams, lakes, and
estuarine-marine shorelines. Riparian
areas are transitional between terrestrial
and aquatic ecosystems, through which
surface and subsurface hydrology
connects waterbodies with their
adjacent uplands. Riparian areas
provide a variety of ecological functions
and services and help improve or
maintain local water quality. (See
general condition 20.)
Shellfish seeding: The placement of
shellfish seed and/or suitable substrate
to increase shellfish production.
Shellfish seed consists of immature
individual shellfish or individual
shellfish attached to shells or shell
fragments (i.e., spat on shell). Suitable
substrate may consist of shellfish shells,
shell fragments, or other appropriate
materials placed into waters for
shellfish habitat.
Single and complete project: The term
‘‘single and complete project’’ is defined
at 33 CFR 330.2(i) as the total project
proposed or accomplished by one
owner/developer or partnership or other
association of owners/developers. A
single and complete project must have
independent utility (see definition). For
linear projects, a ‘‘single and complete
project’’ is all crossings of a single water
of the United States (i.e., a single
waterbody) at a specific location. For
linear projects crossing a single
waterbody several times at separate and
distant locations, each crossing is
considered a single and complete
project. However, individual channels
in a braided stream or river, or
individual arms of a large, irregularly
shaped wetland or lake, etc., are not
separate waterbodies, and crossings of
such features cannot be considered
separately.
Stormwater management: Stormwater
management is the mechanism for
controlling stormwater runoff for the
purposes of reducing downstream
erosion, water quality degradation, and
flooding and mitigating the adverse
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11197
effects of changes in land use on the
aquatic environment.
Stormwater management facilities:
Stormwater management facilities are
those facilities, including but not
limited to, stormwater retention and
detention ponds and best management
practices, which retain water for a
period of time to control runoff and/or
improve the quality (i.e., by reducing
the concentration of nutrients,
sediments, hazardous substances and
other pollutants) of stormwater runoff.
Stream bed: The substrate of the
stream channel between the ordinary
high water marks. The substrate may be
bedrock or inorganic particles that range
in size from clay to boulders. Wetlands
contiguous to the stream bed, but
outside of the ordinary high water
marks, are not considered part of the
stream bed.
Stream channelization: The
manipulation of a stream’s course,
condition, capacity, or location that
causes more than minimal interruption
of normal stream processes. A
channelized stream remains a water of
the United States.
Structure: An object that is arranged
in a definite pattern of organization.
Examples of structures include, without
limitation, any pier, boat dock, boat
ramp, wharf, dolphin, weir, boom,
breakwater, bulkhead, revetment,
riprap, jetty, artificial island, artificial
reef, permanent mooring structure,
power transmission line, permanently
moored floating vessel, piling, aid to
navigation, or any other manmade
obstacle or obstruction.
Tidal wetland: A tidal wetland is a
wetland (i.e., water of the United States)
that is inundated by tidal waters. The
definitions of a wetland and tidal waters
can be found at 33 CFR 328.3(b) and 33
CFR 328.3(f), respectively. Tidal waters
rise and fall in a predictable and
measurable rhythm or cycle due to the
gravitational pulls of the moon and sun.
Tidal waters end where the rise and fall
of the water surface can no longer be
practically measured in a predictable
rhythm due to masking by other waters,
wind, or other effects. Tidal wetlands
are located channelward of the high tide
line, which is defined at 33 CFR
328.3(d).
Vegetated shallows: Vegetated
shallows are special aquatic sites under
the 404(b)(1) Guidelines. They are areas
that are permanently inundated and
under normal circumstances have
rooted aquatic vegetation, such as
seagrasses in marine and estuarine
systems and a variety of vascular rooted
plants in freshwater systems.
Waterbody: For purposes of the
NWPs, a waterbody is a jurisdictional
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water of the United States that, during
a year with normal patterns of
precipitation, has water flowing or
standing above ground to the extent that
an ordinary high water mark (OHWM)
or other indicators of jurisdiction can be
determined, as well as any wetland area
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(see 33 CFR 328.3(b)). If a jurisdictional
wetland is adjacent—meaning
bordering, contiguous, or neighboring—
to a jurisdictional waterbody displaying
an OHWM or other indicators of
jurisdiction, that waterbody and its
adjacent wetlands are considered
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together as a single aquatic unit (see 33
CFR 328.4(c)(2)). Examples of
‘‘waterbodies’’ include streams, rivers,
lakes, ponds, and wetlands.
[FR Doc. E7–3960 Filed 3–9–07; 8:45 am]
BILLING CODE 3710–92–P
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Agencies
[Federal Register Volume 72, Number 47 (Monday, March 12, 2007)]
[Notices]
[Pages 11092-11198]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-3960]
[[Page 11091]]
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Part II
Department of Defense
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Department of the Army, Corps of Engineers
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Reissuance of Nationwide Permits; Notice
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 /
Notices
[[Page 11092]]
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DEPARTMENT OF DEFENSE
Department of the Army, Corps of Engineers
[ZRIN 0710-ZA02]
Reissuance of Nationwide Permits
AGENCY: Army Corps of Engineers, DoD.
ACTION: Final notice.
-----------------------------------------------------------------------
SUMMARY: The U.S. Army Corps of Engineers (Corps) is reissuing all
existing nationwide permits (NWPs), general conditions, and
definitions, with some modifications. The Corps is also issuing six new
NWPs, two new general conditions, and 13 new definitions. The effective
date for the new and reissued NWPs will be March 19, 2007. These NWPs
will expire on March 18, 2012. The NWPs will protect the aquatic
environment and the public interest while effectively authorizing
activities that have minimal individual and cumulative adverse effects
on the aquatic environment.
DATES: The NWPs and general conditions will become effective on March
19, 2007.
ADDRESSES: U.S. Army Corps of Engineers, Attn: CECW-CO, 441 G Street
NW., Washington, DC 20314-1000.
FOR FURTHER INFORMATION CONTACT: Mr. David Olson at 202-761-4922 or by
e-mail at david.b.olson@usace.army.mil or access the U.S. Army Corps of
Engineers Regulatory Home Page at https://www.usace.army.mil/inet/
functions/cw/cecwo/reg/.
SUPPLEMENTARY INFORMATION:
Background
In the September 26, 2006, issue of the Federal Register (71 FR
56258), the U.S. Army Corps of Engineers (Corps) published its proposal
to reissue 43 existing nationwide permits (NWPs) and issue six new
NWPs. The Corps also proposed to reissue its general conditions and add
one new general condition.
The Corps proposal is intended to simplify the NWP program while
continuing to provide environmental protection, by ensuring that the
NWPs authorize only those activities that have minimal individual and
cumulative adverse effects on the aquatic environment and satisfy other
public interest factors.
As a result of the comments received in response to the September
26, 2006, proposal, we have made a number of changes to the NWPs,
general conditions, and definitions to further clarify the permits,
facilitate their administration, and strengthen environmental
protection. These changes are discussed in the preamble.
The Corps is reissuing the 43 existing NWPs, issuing six new NWPs,
reissuing 26 existing general conditions, and issuing one new general
condition. The Corps is also reissuing many of the NWP definitions, and
providing 13 new definitions. The effective date for these NWPs,
general conditions, and definitions is March 19, 2007. These NWPs,
general conditions, and definitions expire on March 18, 2012.
While the Administrative Procedure Act requires a substantive rule
to be published in the Federal Register at least 30 days before its
effective date, exceptions to this requirement can be made for good
cause (5 U.S.C. 553(d)(3)). We are utilizing this good cause exception
to reduce hardships on the regulated public.
Grandfather Provision for Expiring NWPs
In accordance with 33 CFR 330.6(b), activities authorized by the
current NWPs issued on January 15, 2002, that have commenced or are
under contract to commence by March 18, 2007, will have until March 18,
2008, to complete the activity under the terms and conditions of the
current NWPs.
Clean Water Act Section 401 Water Quality Certifications (WQC) and
Coastal Zone Management Act (CZMA) Consistency Determinations
In the September 26, 2006, Federal Register notice and concurrent
with letters from Corps Districts to the appropriate state agencies,
the Corps requested initial 401 certifications and CZM consistency
determinations. This began the Clean Water Act section 401 water
quality certification (WQC) and Coastal Zone Management Act (CZMA)
consistency determination processes.
Today's Federal Register notice begins the 60-day period for
states, Indian Tribes, and EPA to complete their WQC process for the
NWPs. This Federal Register notice also provides a 60-day period for
coastal states to complete their CZMA consistency determination
processes. This 60-day period will end on May 11, 2007.
While the states, Indian Tribes, and EPA complete their WQC
processes and the states complete their CZMA consistency determination
processes, the use of an NWP to authorize a discharge into waters of
the United States is contingent upon obtaining individual water quality
certification or a case-specific WQC waiver. Likewise, the use of an
NWP to authorize an activity within, or outside, a state's coastal zone
that will affect land or water uses or natural resources of that
state's coastal zone, is contingent upon obtaining an individual CZMA
consistency determination, or a case-specific presumption of CZMA
concurrence. We are taking this approach to reduce the hardships on the
regulated public that would be caused by a substantial gap in NWP
coverage if we were to wait 60 days before these NWPs would become
effective.
After the 60-day period, the latest version of any written position
take by a state, Indian tribe, or EPA on its WQC for any of the NWPs
will be accepted as the state's final position on those NWPs. If the
state, Indian tribe, or EPA takes no action by May 11, 2007, WQC will
be considered waived for those NWPs.
After the 60-day period, the latest version of any written position
take by a state on its CZMA consistency determination for any of the
NWPs will be accepted as the state's final position on those NWPs. If
the state takes no action by May 11, 2007, CZMA concurrence will be
presumed for those NWPs.
Discussion of Public Comments
I. Overview
In response to the September 26, 2006, Federal Register notice, we
received more than 22,500 comments. We reviewed and fully considered
all comments received in response to that notice.
General Comments
Many commenters provided general support for the proposal, and some
of them stated that the changes are a step forward in improving
consistency in the NWP program. Some commenters said that the proposed
NWPs provide a balance between environmental protection and allowing
development to occur. One commenter said that the NWP program provides
sufficient environmental protection, through its general conditions and
the ability for the district engineer to exercise discretionary
authority to require individual permits. Several commenters stated that
the proposed NWPs are simpler, clearer, and easier to understand. Three
commenters said that further streamlining is necessary. One commenter
recommended adopting a standard numbering system for paragraphs and
subparagraphs within the NWP text. Three commenters said that the Corps
should retain appropriate references to general conditions in the text
of NWPs, for purpose of clarification.
To the extent that it is feasible, we have adopted a standard
format for the
[[Page 11093]]
NWPs. Some NWPs require different formats, to make them easier to read
and provide further clarification. For the most part, it is not
necessary to retain references to general conditions in the text of the
NWPs, except for general condition 27, Pre-Construction Notification,
because most general conditions apply to all NWPs.
In contrast, a few commenters said that the proposed NWPs are not
simpler and clearer. Three commenters declared that the proposed NWPs
are more like individual permits than general permits. A number of
commenters asserted that the proposed NWPs will significantly increase
costs and delays for permit applicants. Four commenters said that the
attempt at clarification and simplicity will reduce the flexibility of
the NWP program.
The NWPs issued today are not similar to individual permits. The
NWPs provide a streamlined form of Department of the Army authorization
for those activities that result in minimal individual and cumulative
adverse effects on the aquatic environment and satisfy other public
interest review factors. In 2003, the average processing time for NWPs
was 27 days and for individual permits it was 144 days. In response to
comments received as a result of the September 26, 2006, Federal
Register notice, we have modified some of the proposed NWPs to address
provisions that could have unnecessary negative effects on regulatory
efficiency and environmental protection.
Other commenters expressed general opposition to the proposal, and
said that the proposal weakens protection for waters and should be
withdrawn. Many of these commenters objected to the goals of
``streamlining'' or ``improving regulatory efficiency,'' stating that
the focus of the NWPs should be on compliance with the Clean Water Act.
Some commenters expressed opposition to the issuance of the NWPs, and
said that activities proposed for NWP authorization should be
individually subjected to a public notice and comment process. One
commenter suggested that pre-construction notifications should be
posted on district web sites for at least 30 days before an NWP
verification is issued, to allow for public comment on those proposed
activities.
The NWPs issued today comply with the requirements of the Clean
Water Act. When the Clean Water Act was amended in 1977, Congress
recognized the importance of general permits for the effective and
efficient implementation of section 404. We do not agree that pre-
construction notifications should be posted on the Internet for a
public comment period. The review of pre-construction notifications by
district engineers is sufficient for effective environmental
protection. Some NWP activities require coordination with other Federal
and/or State agencies, which provides a supplemental level of
environmental protection. The activities authorized by NWPs have
minimal adverse effects and are limited, within each permit, to
narrowly defined categories of similar activities. Notice and
opportunity for public comment on the authorization of these activities
through NWPs is provided as part of the NWP promulgation process. The
Corps believes this is the appropriate level of public notice and
comment for these types of activities. Further, when reviewing pre-
construction notifications, district engineers will exercise
discretionary authority to require individual permits for those
activities that they determine may result in more than minimal adverse
effects on the aquatic environment or do not satisfy other public
interest review factors, and thus warrant a more thorough individual
review through a public notice and comment process.
Some commenters stated that the NWPs should require consideration
of less damaging alternatives, and others said that the Corps did not
provide sufficient scientific justification for proposed changes to the
NWPs, or demonstrate that NWP activities result in minimal adverse
environmental effects. One commenter said that there is not sufficient
emphasis on avoidance of impacts to waters of the United States.
Another commenter objected to using NWPs to expand existing projects,
stating that it discourages avoidance and minimization.
The NWPs authorize only those activities that result in minimal
individual and cumulative adverse effects on the aquatic environment,
and thus do not include a formal process for consideration of less
damaging alternatives. General condition 20, Mitigation, requires
permittees to avoid and minimize adverse effects to the maximum extent
practicable on the project site. The Corps believes this ensures
sufficient consideration of alternatives for the types of low-impact
projects that are eligible for authorization through NWPs. The Corps
notes that expansion of existing projects may support the goals of
avoidance and minimization, in contrast to the alternative of
developing new sites, which may involve more substantial adverse
impacts. The 404(b)(1) Guidelines contain flexibility for those
activities that result in minimal adverse effects on the aquatic
environment. Compliance with the National Environmental Policy Act and
the Section 404(b)(1) Guidelines is accomplished through decision
documents prepared by the Corps. These decision documents contain
findings that the NWPs result in minimal adverse effects, and are based
on available data at the national scale. Division engineers issue
supplemental decision documents for use of NWPs within Corps district
boundaries.
Several commenters said that the NWPs do not protect small wetlands
and waterbodies enough, and one commenter said that the proposed
permits do not support the ``no overall net loss'' goal for wetlands.
In contrast, one commenter stated that the proposal provides adequate
protection to the environment and supports the ``no overall net loss''
of wetlands goal.
The NWPs protect all jurisdictional waters, including small
wetlands and other waterbodies, through their terms and conditions,
such as acreage limits and linear foot limits. The NWPs also support
the ``no overall net loss goal'' through mitigation requirements,
including aquatic resource restoration, establishment, enhancement, and
preservation activities that may be required as compensatory
mitigation. As noted above, general condition 20, Mitigation, also
includes requirements for on-site avoidance and minimization.
Two commenters objected to allowing district engineers to issue
waivers that allow permittees to exceed the limits of NWPs, stating
that such waivers do not support the minimal adverse effects
requirement. Two commenters said that the NWPs authorize unlimited
impacts to waters of the United States. One commenter remarked that
acreage limits should be consistent for all NWPs. One commenter stated
that the acreage limits in the proposed NWPs are sufficient to ensure
minimal adverse effects. Three commenters asserted that the acreage
limits of the proposed NWPs are too low, and they reduce the
effectiveness of the NWP program. One commenter said that the low
acreage limits for the NWPs lessen incentives to reduce impacts to
waters, since many projects that previously qualified for NWP
authorization now require individual permits. Another commenter stated
that the acreage limits for all NWPs should be based on appropriate
scientific and environmental criteria.
Many of the NWPs have acreage limits, and most of those that do not
are self-limiting due to the nature of the authorized activity (e.g.,
NWP 1 for aids to navigation or NWP 10 for mooring
[[Page 11094]]
buoys). Acreage limits in NWPs cannot be waived by the district
engineer. Linear foot limits in some permits can be waived, but only
for intermittent and ephemeral (not perennial) streams. Two NWPs (i.e.,
NWPs 13 and 36) have cubic yard limits that may be waived. Those NWPs
that contain provisions allowing district engineers to waive linear
foot or cubic yard limits require the district engineer to make a
written determination of minimal adverse effects. In such cases, the
permittee cannot assume that a waiver was granted if the district
engineer does not affirm that waiver in writing (see general condition
27). The Corps believes these limited waiver provisions are appropriate
because activities that exceed the limits may still have minimal
adverse impacts and it may require a site-specific evaluation by the
district engineer to decide if they do. Other NWPs that do not have
limits typically provide environmental benefits, such as aquatic
resource restoration activities authorized by NWP 27 or hazardous and
toxic waste cleanup activities authorized by NWP 38.
NWPs 21, 49, and 50 are a special case, in that they authorize
activities for which review of environmental impacts, including impacts
to aquatic resources, is separately required under other Federal
authorities (e.g., Surface Mining Control and Reclamation Act (SMCRA)
permits for coal mining activities). The Corps believes it would be
unnecessarily duplicative to separately require the same substantive
analyses through an individual permit application as are already
required under SMCRA. However, through the pre-construction
notification review process, the district engineer will consider the
analyses prepared for the SMCRA permit and exercise discretionary
authority to require an individual permit in cases where the district
engineer determines, after considering avoidance and reclamation
activities undertaken pursuant to SMCRA, that the residual adverse
effects are not minimal. The project sponsor is required to obtain
written verification prior to commencing work.
The acreage limits for the NWPs are established so that they
authorize most activities that result in minimal adverse effects on the
aquatic environment. We acknowledge that there may be some activities
that exceed the acreage limits and still have minimal impacts but the
Clean Water Act requires us to ensure that all projects authorized by
NWPs have minimal impacts, not that all minimal-impact projects can be
authorized by NWPs. Activities that are not authorized through NWPs may
be authorized through regional general permits or individual permits.
One commenter stressed that the NWPs must be reissued in time, so
that there is no gap between the expiration date of the current NWPs
and the effective date of the new NWPs. Two commenters recommended
administratively extending the current NWPs until the effective date of
the new NWPs, through 5 U.S.C. 558(c), which is used to
administratively extend National Pollutant Discharge Elimination System
(NDPES) permits issued under Section 402 of the Clean Water Act.
We cannot use 5 U.S.C. 558(c) to administratively extend the NWPs,
since that provision of the Administrative Procedures Act applies only
to activities of ``a continuing nature'' such as discharges of
effluents authorized by National Pollutant Discharge Elimination System
permits issued under Section 402 of the Clean Water Act. The vast
majority of activities authorized by NWPs are construction activities,
with specific start and end dates, either for the discharge of dredged
or fill material into waters of the United States, or structures or
work in navigable waters of the United States. In general, these NWP
activities are not of a continuing nature, and do not meet the
requirements of 5 U.S.C. 558(c). The grandfather provision at 33 CFR
330.6(b) can be used to continue the authorization for those NWP
activities that are under construction, or under contract to begin
construction, after the NWP expires. This provision of the NWP
regulations allows the permittee up to one year to complete the
authorized NWP activity. Today's reissued and new permits will become
effective on March 19, 2007, the day after the existing permits expire.
Thus there will be no gap in coverage. The Corps expects that some
States may be able to make their final Section 401 water quality
certifications for all or some permits by this date. In cases where the
State has not completed a 401 water quality certification by this time,
the Corps will issue provisional verifications and permittees will be
required to obtain individual State certifications prior to commencing
discharges into waters of the United States.
Compliance With Section 404(e) of the Clean Water Act and the 404(b)(1)
Guidelines
Several commenters said that the proposed NWPs are contrary to the
intent of section 404(e) to provide an expedited, streamlined permit
program for activities that have minimal environmental impacts.
The NWPs continue to provide a streamlined authorization process
for those activities that result in minimal individual and cumulative
adverse effects on the aquatic environment. Those activities that do
not qualify for NWP authorization may be authorized by regional general
permits or individual permits.
Many commenters asserted that the NWPs result in more than minimal
adverse effects on the aquatic environment, individually and
cumulatively. Several commenters said that the NWPs do not comply with
the 404(b)(1) Guidelines. One commenter said that the Corps should
provide quantitative statistics on actual impacts, to predict
cumulative impacts resulting from the NWPs. Two commenters believe that
the draft decision documents do not adequately demonstrate that NWPs
will result in minimal individual and cumulative impacts to waters of
the United States. They said that there is not sufficient documentation
to support estimates of the number of times an NWP will be used, the
acres impacted, and the acres mitigated. They also stated that there
should be more specific evaluations of particular types of waters, as
well as landscape considerations. Four commenters said that the Corps
cannot rely on mitigation to ensure minimal adverse effects, stating
that the evaluation of minimal adverse effects must be completed prior
to issuing a general permit. Therefore, the Corps cannot rely on
mitigation that will be offered by permittees when making its finding
under the 404(b)(1) Guidelines.
When we issue the NWPs, we fully comply with the requirements of
the 404(b)(1) Guidelines at 40 CFR 230.7, which govern the issuance of
general permits under section 404. For the section 404 NWPs, each
decision document contains a 404(b)(1) Guidelines analysis. Section
230.7(b) of the 404(b)(1) Guidelines requires only a ``written
evaluation of the potential individual and cumulative impacts of the
categories of activities to be regulated under the general permit.''
Since the required evaluation must be completed before the NWP is
issued, the analysis is predictive in nature. The estimates of
potential individual and cumulative impacts, as well as the projected
compensatory mitigation that will be required, are based on the best
available data from the Corps district offices, based on past use of
NWPs. In our decision documents, we also used readily available
national data on the status of wetlands and other aquatic
[[Page 11095]]
habitats in the United States, and the potential impacts of the NWPs on
those waters.
The 404(b)(1) Guidelines at 40 CFR 230.7 do not prohibit the
consideration of mitigation when making the predictive evaluation of
potential individual and cumulative impacts that may be authorized by
an NWP. The practice of using compensatory mitigation to ensure minimal
adverse individual and cumulative adverse effects is an important
component of the NWP program (see 33 CFR 330.1(e)(3)).
Two commenters said that the Corps cannot rely on regional
conditioning and discretionary authority to ensure minimal adverse
effects. One commenter objected to the ability of the district engineer
to exercise discretionary authority to impose conditions on NWP
activities. Another commenter stated that in order to ensure minimal
adverse effects, pre-construction notification should be required for
all NWPs. A number of commenters said that many of the NWPs do not
authorize activities that are similar in nature. They said that the
Corps is required to explain why activities authorized by an NWP are
similar in nature to warrant authorization under a single NWP.
The pre-construction notification review process and discretionary
authority are important tools to help ensure that the NWPs authorize
only those activities with minimal individual and cumulative adverse
effects. If the district engineer reviews a pre-construction
notification and determines that the impacts are more than minimal,
discretionary authority will be exercised and either the NWP will be
conditioned to require mitigation or other actions to ensure minimal
adverse effects or an individual permit will be required. The Corps
disagrees that pre-construction notification is necessary for all NWP
activities. However, the Corps has expanded the scope of activities
requiring pre-construction notification. Specifically, all activities
conducted under NWPs 7, 8, 17, 21, 29, 31, 33, 34, 37, 38, 39, 40, 42,
44, 45, 46, 49, and 50 now require pre-construction notification,
regardless of acreage impacted. This will enable district engineers to
better ensure that these permits authorize only activities with minimal
impacts.
These NWPs satisfy the requirement under Section 404(e) of the
Clean Water Act that the categories of authorized activities be similar
in nature. The ``similar in nature'' provision does not require NWP
activities to be identical to each other. We believe that the
``categories of activities that are similar in nature'' requirement of
section 404(e) is to be interpreted broadly, for practical
implementation of this general permit program. Nationwide permits, as
well as other general permits, are intended to reduce administrative
burdens on the Corps and the regulated public, by efficiently
authorizing activities that have minimal adverse environmental effects.
For each NWP that authorizes activities under Section 404 of the Clean
Water Act, the 404(b)(1) Guidelines analysis provides a brief
explanation as to why the activities authorized by that NWP are similar
in nature.
One commenter said that consideration of impacts resulting from
general permits should not be limited to the aquatic environment. This
commenter said that Section 404(e) of the Clean Water Act requires
permitted activities to have minimal impacts on the environment as a
whole.
In addition to the requirement that there be no more than minimal
adverse effects on the aquatic environment, activities authorized by
NWPs must also result in minimal adverse effects with regards to the
Corps public interest factors (see 33 CFR 330.1(d)), which include
other components of the environment.
Compliance With the National Environmental Policy Act
Many commenters said that the Corps must complete an Environmental
Impact Statement for the proposed NWPs. One commenter remarked that the
EIS must consider the individual impacts of the NWPs, as well as their
cumulative impacts. One comment asserted that mitigation cannot be used
to justify using an environmental assessment for NEPA compliance,
instead of an Environmental Impact Statement.
The NWPs authorize activities that have minimal individual and
cumulative adverse effects on the aquatic environment and satisfy other
public interest review factors. The NWPs do not reach the level of
significance required for an EIS. The Corps complies with the
requirements of the NEPA by preparing an environmental assessment for
each NWP. When an NWP is issued, a Finding of No Significant Impact is
also issued.
The use of mitigation to make a Finding of No Significant Impact is
a standard practice for NEPA compliance. For the purposes of NEPA,
mitigation includes avoiding impacts, minimizing impacts, rectifying
impacts through repairing or restoring the affected environment,
reducing or eliminating impacts over time through preservation and
maintenance activities, and compensating for impacts by replacing or
providing resources or environments (see 40 CFR 1508.20). Through the
requirements of general condition 20, Mitigation, the review of pre-
construction notifications by district engineers, and regional and
special conditions imposed on the NWPs by division and district
engineers, NWP activities use all these forms of mitigation so that the
adverse effects of the NWPs do not reach the level of significance that
requires an Environmental Impact Statement.
Several commenters stated that the draft decision documents do not
satisfy the requirements of the National Environmental Policy Act
(NEPA). Some commenters said that the analyses in the decision
documents are not based on realistic data. One commenter noted that the
average impact is often much less than the acreage limit for the NWP,
and said that the mitigation ratios seem too high. One commenter said
that the environmental assessments in draft decision documents must
contain site-specific analyses. Two commenters asserted that the
cumulative effects analyses in the decision documents are inadequate.
One commenter said that the cumulative effects analysis should include
information on the past use of NWPs, as well as information on other
development activities expected to have impacts on protected resources.
We believe the data in the draft decision documents comply with the
requirements of NEPA. The estimates of the projected use of the NWPs,
the acres impacted, and the amount of compensatory mitigation are based
on available data from Corps district offices, and other sources of
data, such as surveys. Those data are based on pre-construction
notifications and other requests for NWP verifications for activities
that do not require pre-construction notification. For those NWP
activities that do not require notification, it is necessary to derive
estimates. For the decision documents, we must use predictive data,
since the future use of an NWP is speculative. Likewise, we cannot
provide site-specific information for these environmental assessments,
because there are no specific sites or projects associated with the
proposed issuance of an NWP. Authorized impacts are usually much less
than the acreage limit for an NWP because of the avoidance and
minimization required by the terms and conditions of the NWPs. The
compensatory mitigation data provided in the decision documents include
preservation.
[[Page 11096]]
On June 24, 2005, the Council on Environmental Quality issued
guidance on the consideration of past actions for cumulative effects
analyses. According to this guidance, the cumulative effects analysis
needs to consider relevant past actions that can be used to analyze
reasonably foreseeable effects that have ``a continuing, additive, and
significant relationship to those effects.'' The guidance also
recommends that agencies look at the present effects of past actions
that are relevant because of significant cause-and-effect relationships
with the effects for the proposed action and its alternatives. Except
for a few activities, the NWPs do not authorize activities of a
continuing nature. In general, they authorize construction activities
with specific start and end dates. The NWPs can be issued for only a
period of five years or less, and once an NWP expires, it cannot be
used to authorize activities in waters of the United States. An
activity must then be authorized by the reissued NWP, another NWP, a
regional general permit, or an individual permit. The cumulative
effects analysis is more properly focused on the permits that can be
used to authorize regulated activities, not past permits that have
expired. Therefore, the cumulative effects analysis for the NWP
issuance needs to focus on the reasonably foreseeable cumulative
effects that are expected to occur during the five year period the NWPs
are valid. We use information on past use of the NWPs to estimate how
often an NWP will be used during the period it will be valid, and to
estimate the impacts and compensatory mitigation resulting from the use
of that NWP.
One commenter requested clarification as to whether the draft
decision documents included an environmental assessment, an EIS, or
another type of NEPA document. Two commenters remarked that the Corps
failed to solicit public comment on the environmental assessments for
the proposed NWPs. Two commenters objected to the Finding of No
Significant Impact (FONSI) in each draft decision document, stating
that it is inappropriate to do a FONSI for a proposed action. Another
commenter concurred with the FONSI found in each NWP decision document.
One commenter said that the draft decision documents accurately
analyzed anticipated environmental effects of the proposed NWPs.
A draft environmental assessment was prepared for each of the
proposed NWPs. The draft environmental assessment was in the draft
decision document, along with the draft statement of findings and, if
the NWP authorized activities under Section 404 of the Clean Water Act,
a draft Section 404(b)(1) Guidelines analysis. Those draft decision
documents were available for public review and comment at the same time
as the proposed NWPs, general conditions, and definitions. A number of
commenters who commented on the proposed NWPs also commented on the
draft decision documents. Commenters could also provide input on the
draft FONSI in each decision document.
Compliance With the Endangered Species Act
In the September 26, 2006, Federal Register notice, we stated that
we will conduct Endangered Species Act Section 7(a)(2) consultation for
the NWPs. Since the issuance of the September 26, 2006, proposal, the
Corps has been working with the National Marine Fisheries Service
(NMFS) and the U.S. Fish and Wildlife Service (USFWS) to develop an
analysis plan to guide the formal programmatic Section 7 consultation
for the NWPs. As soon as the analysis plan is completed, the Corps will
request programmatic Endangered Species Act Section 7(a)(2)
consultation with the USFWS and NMFS. Prior to the effective date of
these NWPs, the Corps will issue a section 7(d) determination for the
NWP Program.
Two commenters said the Corps must conduct Endangered Species Act
consultation before the NWPs are issued. One of these commenters said
that the Corps must conduct programmatic section 7 consultation for the
NWP program, with mandatory district-by-district formal consultations.
One commenter requested a timeline for the programmatic Section 7
consultation with the USFWS and NMFS. Another commenter asked for
clarification whether Section 7 ESA consultation will be conducted for
each NWP authorization or the NWP program as a whole. One commenter
objected to the Corps conducting section 7 consultation for coal mining
activities authorized by the Surface Mining Control and Reclamation
Act.
The programmatic ESA consultation will be conducted for the NWP
program as a whole, and will be concluded as expeditiously as possible.
To address ESA compliance while programmatic consultation is being
conducted, a revised Section 7(d) determination will be issued for the
NWP program before the effective date of these NWPs. The Section 7(d)
determination discusses how the issuance of these NWPs will not
foreclose any options. The requirements of general condition 17 and 33
CFR 330.4(f) will ensure compliance with the ESA. We anticipate that
the programmatic consultation will result in a biological opinion that
provides tools that districts can use to better address potential
impacts to the endangered and threatened species that occur in their
areas of regulatory jurisdiction. Corps districts will conduct their
own formal Section 7 consultations as necessary. The programmatic
consultation will be conducted for the NWP program; its applicability
to NWP 21 and other NWPs will be addressed as part of the programmatic
consultation itself.
One commenter said that the Corps cannot rely on permit applicants
to notify them in cases where ESA consultation is necessary. Two
commenters said that the proposed changes to general condition 17,
which requires district engineers to notify prospective permittees of
their ``no effect'' or ``may affect'' determinations within 45 days of
receipt of a complete pre-construction notification, violates the ESA
since the Corps will be unable to make its decision based on the best
available science. Two commenters said that the Corps must require pre-
construction notifications for all NWP activities to help ensure
compliance with the requirements of the ESA. Two other commenters
stated that species-specific regional conditions must be imposed on the
NWPs to protect endangered and threatened species.
Non-federal permittees shall notify the district engineer if any
listed species or designated critical habitat might be affected or is
in the vicinity of the project, or if the project is located in
designated critical habitat, and in such cases shall not begin work on
the activity until notified by the district engineer that the
requirements of the ESA have been satisfied and that the activity is
authorized. This requirement applies even when a pre-construction
notification would not otherwise be required. In such cases, this
condition also prohibits the prospective permittee from conducting the
NWP activity until the district engineer notifies him or her that the
requirements of the ESA have been fulfilled and the activity is
authorized by NWP. The ESA regulations at 50 CFR part 402 do not
require ESA consultation for those activities that will not affect
endangered or threatened species or destroy or modify designated
critical habitat. In some districts, regional conditions will be
imposed on the NWPs to protect listed species and critical habitat.
The notification requirement in general condition 17 does not
violate the ESA. Forty-five days is generally
[[Page 11097]]
sufficient to screen proposed activities for potential effects to
endangered and threatened species or designated critical habitat, and
determine if section 7 consultation is necessary. The notification
requirement will help improve ESA compliance by keeping the prospective
permittee aware of the status of his or her pre-construction
notification and preclude applicants from assuming that they can
proceed after the 45 day pre-construction notification period has
ended, if they have not heard back from the Corps that ESA requirements
have been fulfilled and the activity is authorized. Districts will
continue to develop regional conditions to further protect endangered
and threatened species, as well as critical habitat.
Linear Foot Limits for Stream Bed Impacts
In the September 26, 2006, Federal Register notice, we proposed to
modify several NWPs to include ephemeral streams in the 300 linear foot
limits for losses of stream beds. We also proposed to allow district
engineers to issue written waivers to the 300 linear foot limit for
intermittent and ephemeral streams, upon making a determination that
the adverse effects on the aquatic environment will be minimal. Many
commenters objected to including ephemeral streams in the 300 linear
foot limit for stream beds for NWPs 29, 39, 40, 42, and 43. Many other
commenters supported the proposed change. A large number of commenters
objected to allowing district engineers to waive the 300 linear foot
limit, stating that miles of stream bed could be lost, resulting in
more than minimal adverse environmental effects. A few commenters
supported the proposed waiver. One commenter said that limits to
filling or excavating ephemeral streams should be addressed through the
regional conditioning process, instead of the national terms and
conditions of the NWPs. Another commenter recommended imposing a higher
linear foot limit for losses of ephemeral streams.
Ephemeral streams are important components of the stream network.
Applying the 300 linear foot limit to ephemeral stream beds will help
ensure that the applicable NWPs will authorize activities with minimal
individual and cumulative adverse effects on the aquatic environment.
The ability of district engineers to issue written waivers of the 300
linear foot limit for intermittent and ephemeral stream beds provides
flexibility in the administration of the NWP program. In cases where
the 300 linear foot limit is waived, the acreage limit of the NWP still
applies. We believe it is more appropriate to limit losses of ephemeral
stream beds through the national NWP terms and conditions, to provide
consistent protection for those waters across the country. Regional
differences in the values applied to ephemeral stream functions and
services can be addressed through the waiver process. We believe the
300 linear foot limit, in conjunction with the waiver process, provides
sufficient flexibility for the NWP program while ensuring minimal
adverse effects.
Three commenters recommended that the Corps modify its definition
of ``ephemeral stream'' to simplify the process of distinguishing
between ephemeral and intermittent streams instead of applying the 300
linear foot limit to ephemeral streams. Another commenter indicated
that the difficulty of distinguishing between ephemeral and
intermittent streams is sufficient justification for including
ephemeral streams in the 300 linear foot limit. In contrast, several
commenters stated that including ephemeral streams in the 300 linear
foot limit would not simplify the administration of the NWP program,
because it would result in a large number of individual permits, as
well as substantial increases in the Corps workload. Two commenters
asked the Corps to establish criteria for determining when a waiver of
the 300 linear foot limit can be issued. One commenter stated that the
300 linear foot limit should not apply to filling or excavating
drainage ditches. One of these commenters said that an acreage limit
should be applied to streams, instead of a linear foot limit.
Modifying the definition of ``ephemeral stream'' is not an
appropriate alternative to modifying the 300 linear foot limit. The
definitions of ``ephemeral stream'' and ``intermittent stream'' that
were first promulgated for the NWPs in 2000 are based on the hydrologic
differences between those stream types, especially the differences in
how the stream bed interacts with the water table. We do not agree that
the changes to the 300 linear foot limit will result in a large
increase in the number of individual permits processed per year. Under
the current NWPs, district engineers could exercise discretionary
authority and require individual permits if proposed impacts to
ephemeral streams would be more than minimal. We do not believe it
would be appropriate to establish national criteria for determining
when a waiver of the 300 linear foot limit would be applied. These
determinations should be made on a case-by-case basis by district
engineers, depending upon assessments of site-specific conditions. Even
though the acreage limits of NWPs 29, 39, 40, 42, and 43 also apply to
losses of stream bed, the linear foot limit is a useful tool for
ensuring minimal adverse effects to these linear aquatic ecosystems.
The 300 linear foot limit for filling and excavating stream beds does
not apply to ditches constructed in wetlands, or to ditches constructed
in uplands that are determined to be waters of the United States.
However, the 300 linear foot limit does apply to ditches that are
constructed by modifying streams through channelization or other
activities.
Pre-Construction Notification
Many commenters objected to the proposal to add or expand pre-
construction notification requirements for several NWPs, and a few of
these commenters said that lowering the pre-construction notification
threshold will substantially increase the Corps workload. Several
commenters stated that increasing the number of activities that require
pre-construction notification will result in additional delays and
costs for permit applicants. In contrast, a number of commenters said
that pre-construction notification should be required for all NWP
activities, so that site-specific concerns can be more effectively
addressed. One commenter asserted that the use of the pre-construction
notification process and the use of discretionary authority should be
limited, to provide more certainty to the NWP authorization process.
Another commenter said that the decision to lower pre-construction
notification thresholds should be left to division engineers and the
regional conditioning process, to provide more flexibility for the NWP
program.
Modifying NWPs 39, 40, 42, and 43 to require pre-construction
notification for all activities will help ensure that these NWPs
authorize only those activities that result in minimal individual and
cumulative adverse effects on the aquatic environment and other public
interest review factors, such as flood hazards and floodplain values.
Corps districts have already been receiving large numbers of
verification requests for NWP 39, 40, 42, and 43 activities that do not
require pre-construction notification, so we believe that this change
will not result in a substantial increase in our workload. In addition,
the modified pre-construction notification threshold will facilitate
compliance with the Endangered Species Act and Section 106 of the
National Historic Preservation Act, by better ensuring notice of
activities that
[[Page 11098]]
may have a higher likelihood of affecting endangered or threatened
species, designated critical habitat, or historic properties. We do not
agree that it is necessary to require pre-construction notifications
for all NWP activities, because many NWP activities have negligible
effects on the aquatic environment and the public interest review
factors. We have focused the pre-construction notification requirements
on those activities that have the potential for adverse effects that
may require additional scrutiny by district engineers, including ESA
and/or NHPA consultation.
The pre-construction notification and discretionary authority
processes provide flexibility to the Corps regulatory program, by
allowing the Corps to focus its limited resources on activities that
have the potential to have more than minimal adverse effects on the
aquatic environment. We believe that the proposed changes to the pre-
construction notification thresholds are necessary for effective
implementation of the NWP program, and to address issues of concern at
the national level.
One commenter objected to the increased use of the pre-construction
notification process and the waivers of limits, such as the 300 linear
foot limit for the loss of intermittent and ephemeral stream beds for
certain NWPs, to authorize activities by NWP. Another commenter said
that it is an administrative burden to require the use of NWP 33 with
other NWPs when in-stream construction activities need to occur in dry
conditions. This commenter said that NWP 33 should only be used when
temporary work is done in waters of the United States, and no other NWP
is needed to authorize permanent structures or fills for the activity.
One commenter recommended requiring pre-construction notifications for
filling waters of the United States that are five or more feet deep,
because of the effects on the hydrologic balance of a region.
The ability to waive limits after the review of a pre-construction
notification and a written determination that the adverse effects of a
particular NWP activity will be minimal provides flexibility to the NWP
program, and allows the Corps to focus more of its resources on those
activities that require individual permits and may have substantial
adverse effects on the aquatic environment and the public interest. In
the final NWPs, we have addressed the concern regarding the requirement
to use NWP 33 for all temporary construction, access, and dewatering
activities. Those changes are discussed in further detail for each
applicable NWP. Many NWP activities that result in a discharge of
dredged or fill material into waters of the United States, regardless
of water depth, require pre-construction notification, which will allow
district engineers to review those activities on a case-by-case basis
and assess potential effects on the hydrologic balance of the area in
the vicinity of the proposed work.
One commenter said that the pre-construction notification process
should be modified to require notification of Indian Tribes, to provide
them with the opportunity to comment on proposed activities that may
result in the violation of Indian rights. This commenter also said that
if the Indian Tribe identifies a potential conflict with Federally-
protected Indian rights, the use of the NWPs should not be allowed.
The regional conditioning process, as well as government-to-
government consultation between Tribes and the Corps districts where
Tribal lands are located, are more appropriate mechanisms to address
this commenter's concerns, since there are over 580 Federally-
recognized tribes, and each Tribe is likely to have different concerns
regarding the implementation of the NWP program. General condition 16
states that no NWP activity may impair reserved Tribal rights.
Activities that do impair reserved Tribal rights are not authorized by
NWPs. Regional conditions are an effective mechanism for addressing the
concerns of a specific Indian Tribe, and can be used to facilitate
working relationships between the Corps and the Tribe to help the Corps
fulfill its trust responsibilities.
Clean Water Act Jurisdiction
On June 19, 2006, the Supreme Court issued its decision in the case
of Rapanos et ux, et al, v. United States. Many commenters cited this
decision, as well as other court decisions, and said that the proposed
NWPs exceed the Corps jurisdictional authority under Section 404 of the
Clean Water Act. Several commenters said that ephemeral streams are not
subject to Clean Water Act jurisdiction and should not be covered in
the NWPs. Another commenter asserted that intermittent streams are not
waters of the United States.
The Rapanos decision, as well as other court decisions made in the
past several years, raises questions about the jurisdiction of the
Clean Water Act, including Section 404, over some intermittent and
ephemeral streams and their adjacent wetlands. The Corps will assess
jurisdiction regarding such waters on a case-by-case basis in
accordance with evolving case law and any future guidance that may be
issued by appropriate Executive Branch agencies (e.g., the Corps, U.S.
Environmental Protection Agency). Under the current regulations and
guidance, intermittent and ephemeral streams may meet the regulatory
definition of ``waters of the United States'' and be subject to Clean
Water Act jurisdiction. Regulatory jurisdiction over these waterbodies
will be determined on a case-by-case basis by district engineers, in
accordance with current and future regulations and guidance.
One commenter said that when applying the NWP acreage limits to
wetlands, the Corps should not include all wetlands, just those subject
to Clean Water Act jurisdiction. One commenter stated that a clearer
definition of ``navigable waters'' is needed. Another commenter said
that ditches are not waters of the United States, and impacts to
ditches should instead be addressed through state programs. A commenter
stated that the Corps must promulgate regulations to define ``waters of
the United States'' for the purposes of implementing the NWP program.
The acreage limits of the NWPs apply only to losses of waters of
the United States, including jurisdictional wetlands (see the
definition of the term ``loss of waters of the United States'' in the
``Definitions'' section of the NWPs). Similarly, linear foot limits
apply only to jurisdictional streams. Ditches may also be subject to
jurisdiction under Section 404 of the Clean Water Act and/or Section 10
of the Rivers and Harbors Act of 1899, if they meet the regulatory
definitions of ``waters of the United States'' and/or ``navigable
waters of the United States.'' Waters of the United States are defined
at 33 CFR part 328 and navigable waters of the United States are
defined at 33 CFR part 329.
Regional Conditioning of Nationwide Permits
One commenter stated that regional conditions are unnecessary, and
result in too much restriction of the NWPs. A commenter remarked that
placing too many regional conditions on the NWPs is contrary to E.O.
13274, Environmental Stewardship and Transportation Infrastructure
Project Reviews. One commenter said that regional conditions should not
be redundant with the requirements of other agencies, and the
streamlining objective of the NWPs should be maintained.
Regional conditions are necessary to account for regional
differences in aquatic resource functions, services, and values and to
ensure that the NWPs
[[Page 11099]]
authorize only those activities that have minimal individual and
cumulative adverse effects on the aquatic environment and other public
interest review factors. Regional conditions are important tools for
protecting endangered and threatened species, designated critical
habitat for those species, essential fish habitat, historic properties,
and other important resources. As a general matter, we agree that
regional conditions should not duplicate the requirements of other
agencies, but the Corps often has the responsibility to comply with
other statutes and regulations administered by other agencies.
Two commenters said that there needs to be clearer rules for the
adoption of regional conditions for the NWPs. A couple of commenters
indicated that districts need to provide justifications for proposed
regional condition, and make that information available to the public.
Three commenters said that regional conditions should not be limited to
further restricting the use of the NWPs. One commenter said that
regional conditions should not be based on district boundaries.
Instead, they should be based on ecoregions or other ecologically-
delineated areas. Another commenter recommended that the Corps work
with other agencies to develop a list of high value wetlands in which
NWPs cannot be used.
Regional conditions may only further condition or restrict the
applicability of an NWP (see 33 CFR 330.1(d)). In areas where
environmental conditions and other circumstances warrant less
restrictive general permit conditions, district engineers may issue
regional general permits to authorize similar activities, as long as
those general permits meet applicable requirements. The regulations
governing the adoption of regional conditions are provided at 33 CFR
330.5(c). We believe it is necessary to provide flexibility to division
engineers to determine the necessity and appropriateness of regional
conditions to address concerns regarding the use of NWPs in a
particular area. The notices issued by Corps districts soliciting
public comment on proposed regional conditions are required to include
statements concerning the environmental factors or other public
interest factors resulting in the need for regional conditions (see 33
CFR 330.5(c)(1)). Regional conditions may be based on geographic areas
other than district boundaries. Regional conditions may be imposed on
the use of NWPs in watersheds, counties, states, ecoregions, or other
types of areas. General condition 19, designated critical resource
waters, provides a national list of high value waters. Districts can
coordinate with other agencies to develop lists of high value wetlands
within their district boundaries.
Data Collection
One commenter said that the supporting data used by the Corps falls
short of the standards required by the Data Quality Act of 2001, and
the Office of Management and Budget's ``Guidelines for Ensuring and
Maximizing the Quality, Objectivity, Utility, and Integrity of
Information Disseminated by Federal Agencies.'' This commenter stated
that the Corps should provide data on aquatic resource functions to
support its minimal impact determinations.
The data used for the NWP decision documents are the best available
data at a national scale. The estimated impacts and mitigation provided
in the decision documents were developed by reviewing and analyzing
permit data from our district offices, as well as through consideration
of how proposed changes to the NWPs would affect the amounts of
authorized impacts and mitigation. Data on aquatic resource functions
is generally not available. The National Wetland Inventory examines
wetland status and trends for the conterminous United States, but
information on wetland quality and function is not available.
Three commenters expressed concern about tracking permanent and
temporary impacts to waters of the United States and recommended that
the Corps implement a national tracking and monitoring system. This
system would also facilitate the sharing of information with
cooperating resource agencies and help improve decision making.
We are in the process of transitioning to a new automated
information system (AIS) for the Corps regulatory program. The new AIS
is version 2.0 of the ``OMBIL Regulatory Module'' (ORM 2.0). This
national tracking and monitoring system will improve and standardize
data collection for the Corps regulatory program, and will assist in
decision-making for permit actions and other types of regulatory
activities, such as jurisdictional determinations. ORM 2.0 will be
spatially enabled, using geographic information systems and other
analytical tools that will provide more efficient and effective
processing of permit applications, jurisdictional determinations, and
other tasks. Cumulative impact analysis will also be supported by ORM
2.0. The structure of ORM 2.0 will also be standard among Corps
districts, providing for more consistent information collection and
storage, and will be readily available for analysis and reporting. The
standard structure of ORM will also promote consistency in Regulatory
Program implementation.
ORM 2.0 will help improve data collection for the NWP program, as
well as other types of permits issued by the Corps. Data collection
will be more standard among permit types, especially for impact and
mitigation data. We will continue to collect data on authorized losses
of waters of the United States, including resource type, acreage, and
impact type. ORM 2.0 incorporates several additional AIS resources to
assist in the tracking of all required compensatory mitigation,
including the amount, type (e.g., reestablishment), and source (i.e.,
permittee-responsible mitigation, mitigation bank, or in-lieu fee).
ORM 2.0 will also facilitate compliance with the Endangered Species
Act, the National Historic Preservation Act, and the essential fish
habitat provisions of the Magnuson-Stevens Fishery Management and
Conservation Act. Screening tools based on available data for those
resources will help Corps personnel identify activities that may affect
those resources and require further consultation. The available
resource data will be provided by other agencies, through data sharing
agreements. Available data sets from the national, state, and local
levels can be utilized by ORM 2.0.
ORM 2.0 is capable of supporting electronic interagency
coordination. For activities that typically require interagency
coordination and consultation, agencies will have the option of
receiving electronic coordination notices and consultation requests and
of responding to the Corps via a link to ORM 2.0. Agencies will be
required to enter into a Memorandum of Agreement supporting the use of
electronic communications for permit activities.
ORM 2.0 will also include time tracking features to help remind
Corps project managers when the end of the 45-day pre-construction
notification review will occur. Monitoring and enforcement activities
will also be supported by ORM 2.0, including the tracking of when
monitoring reports for compensatory mitigation projects are due.
ORM 2.0 will also support an electronic permit application, thereby
allowing prospective permittees to submit their pre-construction
notifications electronically to the appropriate Corps district. Permit
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applicants will be able to check the status of their permit
applications through the electronic permit Web site.
Other Issues
One commenter said that the Corps should stop issuing NWPs until
effective compensatory mitigation is provided for those permits.
Several commenters stated that the Corps places too much reliance on
compensatory mitigation, citing recent studies that concluded that
compensatory mitigation projects often fail to achieve their
objectives. A couple of commenters asserted that the Corps should not
rely on compensatory mitigation to ensure minimal individual and
cumulative adverse effects. Another commenter objected to the more
stringent requirements for compensatory mitigation for NWP activities,
stating that compensatory mitigation for small impacts tends to be more
expensive than the costs to plan and construct the proposed activity
requiring NWP authorization.
Compensatory mitigation is an important mechanism to help ensure
that the NWPs authorize activities that result in minimal individual
and cumulative adverse effects on the aquatic environmental. We
acknowledge that the ecological success of compensatory mitigation
projects varies widely. Some compensatory mitigation projects fail to
meet their objectives, while others do result in successful replacement
of aquatic resource functions that are lost as a result of activities
authorized by NWPs. We are committed to improving compliance for
compensatory mitigation required for Department of the Army permits,
including NWPs. District engineers have the flexibility to determine
when compensatory mitigation should be required for activities
authorized by NWPs. If it is not appropriate or practicable to require
compensatory mitigation for a particular activity, and that activity
will result in minimal adverse effects on the aquatic environment, then
the district engineer may determine that compensatory mitigation is not
necessary. Otherwise, if the proposed activity will result in more than
minimal adverse effects on the aquatic environment after determining
that compensatory mitigation is not appropriate or practicable, then an
individual permit would be required.
One commenter said that the NWPs do not distinguish between
different types of waters, but combine waters when applying the acreage
limit for the NWP. This commenter stated that the Corps needs to
recognize that different types of waters often have different
functions.
The NWPs do recognize different types of waters. The terms and
conditions of NWPs are often based on the characteristics of different
types of waters. For example, NWP 39 does not authorize discharges of
dredged or fill into non-tidal wetlands adjacent to tidal waters.
One commenter said that the requirement for NWP activities to be
single and complete projects should not be removed, citing the proposed
changes to NWPs 13, 15, 18, and 19. This commenter stated that the
requirement for single and complete projects does not appear outside of
the Corps definition at 33 CFR 330.2(i). One commenter objected to the
removal of the requirement in several NWPs to submit an avoidance/
minimization statement with the pre-construction notification.
The requirement that NWPs authorize single and complete projects
applies to all NWPs. Limiting the NWPs to authorize only single and
complete projects is a long-standing practice, and we are adding a new
general condition (GC 28) to clarify that the NWPs only authorize
single and complete projects.
The requirement for an avoidance/minimization statement that was in
NWPs 39, 43, and 44 is not necessary, because we have modified NWP 39
to require pre-construction notification for all activities, and we are
requiring pre-construction notification for all construction and
expansion of storm water management facilities under NWP 43. In
addition, general condition 20 requires permittees to avoid and
minimize adverse effects to waters of the United State to the maximum
extent practicable on the project site. When reviewing a pre-
construction notification, the district engineer will determine whether
sufficient avoidance and minimization of impacts to waters of the
United States has occurred, and whether the activity complies with
general condition 20. It is the responsibility of the district engineer
to make this determination, and we do not believe it is appropriate to
place that burden on the prospective permittee by requiring the
submittal of