Oil and Gas; Hydraulic Fracturing on Federal and Indian Lands; Rescission of a 2015 Rule, 61924-61949 [2017-28211]
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Federal Register / Vol. 82, No. 249 / Friday, December 29, 2017 / Rules and Regulations
DEPARTMENT OF THE INTERIOR
Bureau of Land Management
43 CFR Part 3160
[LLWO300000 L13100000 PP0000 18X]
RIN 1004–AE52
Oil and Gas; Hydraulic Fracturing on
Federal and Indian Lands; Rescission
of a 2015 Rule
Bureau of Land Management,
Interior.
ACTION: Final rule.
AGENCY:
On March 26, 2015, the
Bureau of Land Management (BLM)
published in the Federal Register a final
rule entitled, ‘‘Oil and Gas; Hydraulic
Fracturing on Federal and Indian
Lands’’ (2015 rule). With this final rule,
the BLM is rescinding the 2015 rule
because we believe it imposes
administrative burdens and compliance
costs that are not justified. This final
rule returns the affected sections of the
Code of Federal Regulations (CFR) to the
language that existed immediately
before the published effective date of
the 2015 rule (June 24, 2015), except for
changes to those regulations that were
made by other rules published between
the date of publication of the 2015 rule
and now, and the phrase ‘‘perform
nonroutine fracturing jobs,’’ which is
not restored to the list of subsequent
operations requiring prior approval.
None of the changes by other rules are
relevant to this rulemaking.
DATES: This final rule is effective on
December 29, 2017.
FOR FURTHER INFORMATION CONTACT:
Lorenzo Trimble, Acting Division Chief,
Fluid Minerals Division, 202–912–7342,
for information regarding the substance
of this final rule or information about
the BLM’s Fluid Minerals program.
Persons who use a telecommunications
device for the deaf (TDD) may call the
Federal Relay Service (FRS) at 1–800–
877–8339, 24 hours a day, 7 days a
week, to leave a message or question
with the above individuals. You will
receive a reply during normal hours.
SUPPLEMENTARY INFORMATION:
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SUMMARY:
Executive Summary
Pursuant to the Mineral Leasing Act
(MLA), the Federal Land Policy and
Management Act (FLPMA), the Indian
mineral leasing laws, and other legal
authorities, the BLM is charged with
administering oil and gas operations on
Federal and Indian lands in a manner
that allows for responsible and
appropriate resource development. This
final rule is needed to prevent the
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unnecessarily burdensome and
unjustified administrative requirements
and compliance costs of the 2015 rule
from encumbering oil and gas
development on Federal and Indian
lands.
The process known as ‘‘hydraulic
fracturing’’ has been used by the oil and
gas industry since the 1950s to stimulate
production from oil and gas wells. In
recent years, public awareness of the
use of hydraulic fracturing practices has
grown. New horizontal drilling
technology has allowed increased access
to oil and gas resources in tight shale
formations across the country,
sometimes in areas that have not
previously experienced significant oil
and gas development. As hydraulic
fracturing has become more common,
public concern increased about whether
hydraulic fracturing contributes to or
causes the contamination of
groundwater sources, whether the
chemicals used in hydraulic fracturing
should be disclosed to the public, and
whether there is adequate management
of well integrity and of the ‘‘flowback’’
fluids that return to the surface during
and after hydraulic fracturing
operations.
On March 26, 2015, the BLM
published in the Federal Register a final
rule entitled, ‘‘Oil and Gas; Hydraulic
Fracturing on Federal and Indian
Lands’’ (80 FR 16128) (2015 rule). The
2015 rule was intended to: Ensure that
wells are properly constructed to protect
water supplies, make certain that the
fluids that flow back to the surface as a
result of hydraulic fracturing operations
are managed in an environmentally
responsible way, and provide public
disclosure of the chemicals used in
hydraulic fracturing fluids. To achieve
its objectives, the 2015 rule required oil
and gas operators to:
• Obtain the BLM’s approval before
conducting hydraulic fracturing
operations by submitting an application
with information and a plan for the
hydraulic fracturing design (43 CFR
3162.3–3(d)(4)).
• Include a hydraulic fracturing
application in applications for permits
to drill (APDs), or in a subsequent
‘‘sundry notice’’ (43 CFR 3162.3–3(c)).
• Include information about the
proposed source of water in each
hydraulic fracturing application so that
the BLM can complete analyses required
by the National Environment Policy Act
(NEPA) (43 CFR 3162.3–3(d)(3)).
• Include available information about
the location of nearby wells to help
prevent ‘‘frack hits’’ (i.e., unplanned
surges of pressurized fluids into other
wells that can damage the wells and
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equipment and cause surface spills) (43
CFR 3162.3–3(d)(4)(iii)(C)).
• Verify that the well casing is
surrounded by adequate cement, and
test the well to make sure it can
withstand the pressures of hydraulic
fracturing (43 CFR 3162.3–3(e)(1) and
(2) and (f)).
• Isolate and protect usable water,
while redefining ‘‘usable water’’ to
expressly defer to classifications of
groundwater by states and tribes, and
the Environmental Protection Agency,
43 CFR 3160.0–7; and require
demonstrations of 200 feet of adequate
cementing between the fractured
formation and the bottom of the closest
usable water aquifer, or cementing to
the surface (43 CFR 3162.3–3(e)(2)(i)
and (ii)).
• Monitor and record the annulus
pressure during hydraulic fracturing
operations, and report significant
increases of pressure (43 CFR 3162.3–
3(g)).
• File post-fracturing reports
containing information about how the
hydraulic fracturing operation actually
occurred (43 CFR 3162.3–3(i)).
• Submit lists of the chemicals used
(non-trade-secrets) to the BLM by
sundry notice (Form 3160–5), to
FracFocus (a public website operated by
the Ground Water Protection Council
and the Interstate Oil and Gas Compact
Commission), or to another BLMdesignated database (43 CFR 3162.3–
3(i)(1)).
• Withhold trade secret chemical
identities only if the operator or the
owner of the trade secret submits an
affidavit verifying that the information
qualifies for trade secret protection (43
CFR 3162.3–3(j)).
• Obtain and provide withheld
chemical information to the BLM, if the
BLM requests the withheld information
(43 CFR 3162.3–3(j)(3)).
• Store recovered fluids in aboveground rigid tanks of no more than 500barrel capacity, with few exceptions,
until the operator has an approved plan
for permanent disposal of produced
water (as required by Onshore Oil and
Gas Order No. 7) (43 CFR 3162.3–3(h)).
The 2015 rule also authorized two
types of variances:
• Individual operation variances to
account for local conditions or new or
different technology (43 CFR 3162.3–
3(k)(1)).
• State or tribal variances to account
for regional conditions or to align the
BLM requirements with state or tribal
regulations (43 CFR 3162.3–3(k)(2)).
For either type of variance to be
approved, the variance needed to meet
or exceed the purposes of the specific
provision of the 2015 rule for which the
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variance is being granted (43 CFR
3162.3–3(k)(3)).
The 2015 rule was immediately
challenged in court. The United States
District Court for the District of
Wyoming stayed the 2015 rule before it
went into effect, and later issued a final
order setting aside the rule, concluding
that it was outside the BLM’s statutory
authority. On appeal, the United States
Court of Appeals for the Tenth Circuit
dismissed the appeal as prudentially
unripe, and vacated the District Court’s
final order with instructions for the
District Court to dismiss the case
without prejudice. The plaintiffs have
moved for rehearing or reconsideration
en banc. Briefing on those petitions is
complete. The Tenth Circuit has not yet
issued its mandate to the District Court,
and thus the 2015 rule has not gone into
effect.
Commenters and a District Court have
raised doubts about BLM’s statutory
authority to regulate hydraulic
fracturing operations on Federal and
Indian lands. The BLM believes that it
is not only better policy to rescind the
2015 rule to relieve operators of
duplicative, unnecessary, costly and
unproductive regulatory burdens, but it
also eliminates the need for further
litigation about BLM’s statutory
authority.
On March 28, 2017, President Trump
issued Executive Order 13783, entitled,
‘‘Promoting Energy Independence and
Economic Growth’’ (82 FR 16093, Mar.
31, 2017), which directed the Secretary
of the Interior to review four specific
rules, including the 2015 rule, for
consistency with the policy set forth in
section 1 of the Order and, if
appropriate, take action to lawfully
suspend, revise, or rescind those rules
that are inconsistent with the policy set
forth in Executive Order 13783.
Section 1 of Executive Order 13783
states that it is in the national interest
to promote clean and safe development
of United States energy resources, while
avoiding ‘‘regulatory burdens that
unnecessarily encumber energy
production, constrain economic growth,
and prevent job creation.’’ Section 1
states that the prudent development of
these natural resources is ‘‘essential to
ensuring the Nation’s geopolitical
security.’’ Section 1 finds that it is in the
national interest to ensure that
electricity is affordable, reliable, safe,
secure, and clean, and that coal, natural
gas, nuclear material, flowing water, and
other domestic sources, including
renewable sources, can be used to
produce it.
Accordingly, Section 1 of Executive
Order 13783 declares that the policy of
the United States is that: (1) Executive
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departments and agencies immediately
review regulations that potentially
burden the development or use of
domestically produced energy resources
and, as appropriate, suspend, revise, or
rescind those that unduly burden
domestic energy resources development
‘‘beyond the degree necessary to protect
the public interest or otherwise comply
with the law’’; and (2) To the extent
permitted by law, agencies should
promote clean air and clean water,
while respecting the proper roles of the
Congress and the States concerning
these matters; and (3) Necessary and
appropriate environmental regulations
comply with the law, reflect greater
benefit than cost, when permissible,
achieve environmental improvements,
and are developed through transparent
processes using the best available peerreviewed science and economics.
To implement Executive Order 13783,
Secretary of the Interior Ryan K. Zinke
issued Secretarial Order No. 3349
entitled, ‘‘American Energy
Independence,’’ on March 29, 2017,
which, among other things, directed the
BLM to proceed expeditiously in
proposing to rescind the 2015 rule.
As directed by Executive Order 13783
and Secretarial Order No. 3349, the
BLM conducted a review of the 2015
rule. As a result of this review, the BLM
believes that the compliance costs
associated with the 2015 rule are not
justified.
In conjunction with its review of the
2015 rule, the BLM analyzed the
potential economic implications of
implementing the 2015 rule and this
final rule that rescinds the 2015 rule.
That analysis is documented in the
regulatory impact analysis (RIA)
document that the BLM prepared for
this final rule. As described in detail in
that RIA, the BLM has estimated that
this final rule will provide a reduction
in compliance costs relative to the 2015
rule of up to $9,690 per well or
approximately $14 million to $34
million per year.
When issuing the 2015 rule, the BLM
acknowledged that it already had ‘‘an
extensive process in place to ensure that
operators conduct oil and gas operations
in an environmentally sound manner’’
and that ‘‘the regulations and Onshore
Orders that have been in place to this
point have served to provide reasonable
certainty of environmentally responsible
development of oil and gas resources’’
(80 FR at 16133 and 16137). However,
in the RIA for the 2015 rule, while
noting that many of the requirements of
the 2015 rule were consistent with
industry practice and that some were
duplicative of state requirements or
were generally addressed by existing
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BLM requirements, the BLM asserted
that the 2015 rule would provide
additional assurance that operators are
conducting hydraulic fracturing
operations in an environmentally sound
and safe manner, and increase the
public’s awareness and understanding
of these operations.
While the extent of the benefits that
the additional assurances might provide
are questionable, it follows that the
rescission of the 2015 rule could
potentially reduce any such assurances.
However, considering state regulatory
programs, the sovereignty of tribes to
regulate operations on their lands, and
the pre-existing Federal regulations, the
proposed rescission of the 2015 rule
would not leave hydraulic fracturing
operations unregulated.
The BLM’s review of the 2015 rule
also included a review of state laws and
regulations that found that most states
are either currently regulating hydraulic
fracturing or are in the process of
establishing hydraulic fracturing
regulations. When the 2015 rule was
issued, 20 of the 32 states with currently
existing Federal oil and gas leases had
regulations addressing hydraulic
fracturing. In the time since the
promulgation of the 2015 rule, an
additional 12 states have introduced
laws or regulations addressing hydraulic
fracturing. As a result, all 32 states with
Federal oil and gas leases currently have
laws or regulations that address
hydraulic fracturing operations.1 In
addition, some tribes with oil and gas
resources have also taken steps to
regulate oil and gas operations,
including hydraulic fracturing, on their
lands.
The BLM also now believes that
disclosure of the chemical content of
hydraulic fracturing fluids to state
regulatory agencies and/or databases
1 The reference to 32 states with existing Federal
oil and gas leases includes the following states:
Alabama, Alaska, Arizona, Arkansas, California,
Colorado, Idaho, Illinois, Indiana, Kansas,
Kentucky, Louisiana, Maryland, Michigan,
Mississippi, Montana, Nebraska, Nevada, New
Mexico, New York, North Dakota, Ohio, Oklahoma,
Oregon, Pennsylvania, South Dakota, Tennessee,
Texas, Utah, Virginia, West Virginia, and Wyoming.
The State of Oregon regulates hydraulic fracturing
operations by way of its regulations addressing
‘‘Water Injection and Water Flooding of Oil and Gas
Properties’’ (Oregon Administrative Rules [Or.
Admin. R.] sec. 632–010–0194). The State of
Arizona regulates hydraulic fracturing operations
under regulations addressing ‘‘Artificial
Stimulation of Oil and Gas Wells’’ (Arizona
Administrative Code [A.A.C.] sec. R12–7–117). The
State of Indiana issued ‘‘emergency rules’’ in 2011
and 2012 that incorporated new legislation
addressing hydraulic fracturing (Pub. L. 140–2011
and Pub. L. 16–2012) into Indiana’s oil and gas
regulations at 312 Indiana Administrative Code
(IAC) Article 16. For further information about the
state regulatory programs, see § 2.12 of the RIA and
Appendix 1 of the EA prepared for this rule.
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such as FracFocus is more prevalent
than it was in 2015 and, therefore, there
is no continuing need for a Federal
chemical disclosure requirement, since
companies are already making those
disclosures on most operations, either to
comply with state law or voluntarily.
There are 25 states that currently use
FracFocus for chemical disclosures.
These include seven states where the
BLM has major oil and gas operations,
including Colorado, Montana, New
Mexico, North Dakota, Oklahoma,
Texas, and Utah.
In addition to state and tribal
regulation of hydraulic fracturing, the
BLM has several pre-existing regulations
that it will continue to rely on, some of
which are set out at 43 CFR subpart
3162 and in Onshore Oil and Gas Orders
1, 2, and 7. These regulations ensure
that operators conduct oil and gas
operations in an environmentally sound
manner and also reduce the risks
associated with hydraulic fracturing by
providing specific requirements for well
permitting; construction, casing, and
cementing; and disposal of produced
water.2 The BLM also possesses
discretionary authority allowing it to
impose site-specific protective measures
reducing the risks associated with
hydraulic fracturing.
Prior to the 2015 rule, the regulations
at 43 CFR 3162.3–2(a) (2014) provided
in pertinent part that a ‘‘proposal for
further well operations shall be
submitted by the operator on Form
3160–5 for approval by the authorized
officer prior to commencing operations
to . . . perform nonroutine fracturing
jobs . . . .’’ In the proposed rule that
preceded this final rule, the BLM
offered to restore the regulatory text in
§ 3162.3–2(a) regarding ‘‘nonroutine
fracturing jobs’’ to exactly as it existed
in the pre-2015 rule regulations. Those
regulations, however, did not define
‘‘nonroutine fracturing jobs’’ or provide
guidance to operators or BLM
authorized officers on how to
distinguish ‘‘routine’’ from
‘‘nonroutine.’’ Some of the comments
that were submitted for the proposed
rule noted this and criticized the
regulations for being vague, confusing,
and difficult for operators and the BLM
to apply. In light of these comments, the
BLM reconsidered its initial proposal to
restore the regulation text in section
3162.3–2(a) requiring prior approval for
‘‘nonroutine fracturing jobs.’’
As a result of considerable advances
in oil and gas development technology
2 Additional discussion regarding Onshore Oil
and Gas Orders 1, 2, and 7, and 43 CFR subpart
3162, is provided in § 2.11 of the RIA and the EA
prepared for this rule.
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in the last 20 years, hydraulic fracturing
practices that would have been
considered ‘‘nonroutine’’ when the BLM
originally issued the regulations
requiring prior approval for ‘‘nonroutine
fracturing jobs’’ are now commonly
utilized and considered ‘‘routine.’’ The
combination of advances in oil and gas
development technology and the BLM’s
existing authority to mitigate the
potential risks of hydraulic fracturing
operations through site-specific
protective measures that are applied as
a part of the environmental review and
approval process at the APD stage has
made post-APD approvals for
‘‘nonroutine fracturing jobs’’ at most a
very rare occurrence. In fact, while the
BLM has not been tracking requests for
approval of ‘‘nonroutine fracturing
jobs,’’ recent inquiries to BLM state
offices have not revealed any examples
of ‘‘nonroutine fracturing’’ requests or
approvals. Thus, given that the
‘‘nonroutine fracturing’’ requirement
has not, and does not seem to serve any
purpose, and removing it from the
regulations could reduce the potential
for unproductive confusion or
paperwork without adverse effects, the
BLM has not restored the ‘‘nonroutine
fracturing’’ requirement in this final
rule.
The BLM’s review of the 2015 rule
also included a review of incident
reports from Federal and Indian wells
since December 2014. This review
indicated that resource damage is
unlikely to increase by rescinding the
2015 final rule because of the rarity of
adverse environmental impacts that
occurred from hydraulic fracturing
operations since promulgation of the
2015 rule. The BLM now believes that
the appropriate framework for
mitigating these impacts exists through
state regulations, through tribal exercise
of sovereignty, and through BLM’s own
pre-existing regulations and authorities
(pre-2015 rule 43 CFR subpart 3162 and
Onshore Orders 1, 2, and 7).
I. Background
II. Discussion of the Final Rule and
Comments on the Proposed Rule
III. Procedural Matters
I. Background
The development and production of
oil and gas, including hydraulic
fracturing operations, are regulated
under a framework of Federal, state, and
local laws, and, on some tribal lands, by
tribal regulations. Several Federal
agencies implement Federal laws and
requirements while each state in which
oil and gas is produced has one or more
regulatory agencies that administer state
laws and requirements.
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State and local laws apply on Federal
lands, except to the extent that they are
preempted by Federal law. Federal
preemption is rare, and is not at issue
in the final rule. Accordingly, the
drilling and completion of oil and gas
wells, including hydraulic fracturing
operations, are subject to Federal and
state and local regulation on Federal
lands. If the requirements of a state
regulation are more stringent than those
of a Federal regulation, for example, the
operator can comply with both the state
and the Federal regulation by meeting
the more stringent state requirement.
Tribal and Federal laws apply to oil
and gas drilling and completion
operations, including hydraulic
fracturing operations, on tribal lands.
Operators on tribal lands can comply
with both tribal and Federal regulations
governing drilling and completion
requirements by complying with the
stricter of those rules.
Regardless of any difference in
operational regulations, operators on
Federal lands must comply with all
Federal, state, and local permitting and
reporting requirements. On Indian
lands, they must comply with all
Federal and tribal permitting and
reporting requirements.
Existing BLM Requirements—Not
Affected by This Final Rule
The BLM has an extensive process in
place to ensure that operators conduct
oil and gas operations in a safe and
environmentally sound manner that
protects resources. The following
discussion provides a description of
some of the BLM’s existing processes
and requirements that are not affected
by the rescission of the 2015 rule
pursuant to this final rule that help to
ensure that the risks of oil and gas
operations, including hydraulic
fracturing, are appropriately minimized.
The BLM applies a tiered decisionmaking approach when providing
access for the development of Federal
oil and gas resources on public lands.
First, the BLM develops land use plans
(the BLM refers to these plans as
Resource Management Plans, or RMPs).
The RMP serves as the basis for all land
use decisions the BLM makes, including
decisions to delineate public lands that
are appropriate for oil and gas leasing.
Establishment or revision of an RMP
requires preparation of an
environmental impact statement (EIS) in
accordance with the National
Environmental Policy Act (NEPA). In
areas where lands are open for oil and
gas leasing, the EIS prepared to support
establishment or revision of the RMP
analyzes oil and gas development
related impacts that may be expected to
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occur over the life of an RMP (typically
20 years). The RMP identifies the terms
and conditions under which the BLM
would allow oil and gas development to
occur in order to protect other resource
values. Those terms and conditions may
include mitigation measures that would
be evaluated through the EIS and are
implemented as stipulations
incorporated into oil and gas leases. If
necessary, certain lands are closed to oil
and gas leasing altogether when such
use is incompatible with sensitive
resources or other planned uses. In
addition to compliance with NEPA, the
BLM must comply with the National
Historic Preservation Act (NHPA), the
Endangered Species Act (ESA), and
other applicable Federal laws and
regulations. Once an RMP has been
approved, the BLM makes land use
decisions, including oil and gas
development decisions, in accordance
with the RMP, or any revisions or
amendments to that RMP.
Before oil and gas activities may occur
on Federal lands, interested parties
must obtain a lease from the BLM. Oil
and gas leases are acquired through an
auction-style sale process in which
interested parties typically identify
tracts of land that they would like to see
leased. The BLM will conduct a
preliminary evaluation to first
determine whether the lands nominated
for oil and gas leasing are under Federal
jurisdiction and are open to leasing in
accordance with the applicable RMP.
The BLM will then conduct a second
tier of NEPA review—typically through
an EA—to address potential impacts
that could be caused by oil and gas
development within the nominated
lease area. The NEPA review conducted
at the leasing stage tiers to the EIS
prepared for the RMP. If the BLM’s
analysis determines that the nominated
tracts are suitable for leasing, the BLM
would offer the tracts for lease during a
competitive oil and gas lease sale
auction. If any of the tracts are not bid
upon during the lease sale auction,
those tracts become available for noncompetitive leasing by the first qualified
applicant for a two year period that
begins on the first business day
following the last day of the lease sale.
In addition to compliance with the
NEPA, the BLM also complies with the
NHPA and the ESA at the leasing stage.
Upon issuance by the BLM, the lease
allows the operator to conduct
operations on the lease subject to the
requirements of existing regulations, the
lease terms and stipulations, and the
requirement that the operator obtain
BLM approval of a site-specific
Application for Permit to Drill (APD).
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When trust or restricted Indian lands
are involved, the tribe or individual
Indian mineral owner plans the uses of
their own lands. They lease their own
oil and gas resources with the consent
of the Department of the Interior’s
(‘‘DOI’’ or ‘‘the Department’’) Bureau of
Indian Affairs (BIA). Nonetheless, the
BLM often serves as a cooperating
agency during the development of the
environmental review for such actions.
Moreover, pursuant to delegations from
the Secretary of the Interior (Secretary)
and BIA regulations, the BLM regulates
oil and gas operations on trust and
restricted Indian lands, applying the
same operating regulations that apply
on Federal lands.
The procedures followed when
issuing leases to develop Indian oil and
gas resources may be similar to, or
different from, the leasing process used
for Federal lands, depending upon a
number of different factors. For
example, when tribal oil and gas
resources are leased under the authority
of the Indian Mineral Leasing Act of
1938 (IMLA), the BIA typically conducts
a competitive lease sale process that
shares many similarities with the
leasing process for Federal lands. In
contrast, the Indian Mineral
Development Act of 1982 (IMDA),
allows Indian mineral owners to forego
the competitive auction-style leasing
process and negotiate directly with
potential operators for agreements to
develop their oil and gas resources.3
However, for both IMLA and IMDA
authorized leases and agreements, the
approval of the Indian mineral owner
and the BIA or the DOI is required.4
Much like with oil and gas leasing
actions involving Federal lands,
authorizations pursuant to the IMLA
and the IMDA to develop Indian oil and
gas resources are subject to compliance
with applicable Federal statutes,
including NEPA. The procedures for
issuing leases and other development
agreements for Indian oil and gas
resources are outlined in the BIA’s
regulations at 25 CFR parts 211 (IMLA
leasing), 212 (agreements for allotted
lands), and 225 (IMDA agreements).
The BLM has existing regulations,
including Onshore Oil and Gas Orders,
to ensure that operators conduct oil and
gas exploration and development in a
3 The IMDA authorizes Indian tribes and
individual Indian mineral owners to enter into
leases, as well as other types of agreements, to
explore for and develop their oil and gas resources.
25 U.S.C. 2102(a). Indian allotted lands may also be
leased for mineral development pursuant to 25
U.S.C. 396.
4 In certain situations, IMDA agreements may
only be approved by the Secretary of the Interior
or the Assistant Secretary for Indian Affairs. See 25
U.S.C. 2103(d) and 25 CFR 225.3.
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safe and environmentally responsible
manner that protects other resources.
Sections 3162.3–1 and Onshore Order 1
require an operator to get approval from
the BLM prior to drilling a well. The
operator must submit an APD
containing all of the information
required by Onshore Order 1. This
includes a completed Form 3160–3,
Application for Permit to Drill or ReEnter, a well plat, a drilling plan, a
surface use plan, bonding information,
and an operator certification.
Upon receiving a drilling proposal on
Federal lands, the BLM is required by
existing section 3162.3–1(g) to post
information for public inspection for at
least 30 days before the BLM can
approve the APD. The information must
include: The company/operator name;
the well name/number; and the well
location described to the nearest
quarter-quarter section (40 acres), or
similar land description in the case of
lands described by metes and bounds,
or maps showing the affected lands and
the location of all tracts to be leased and
of all leases already issued in the
general area.
The public can review the posted
information and provide any input they
would like the BLM to consider during
the environmental analysis the BLM
prepares prior to making a decision on
the APD.
The drilling plan provided by the
operator must be in sufficient detail to
permit the BLM to complete an
appraisal of the technical adequacy of,
and environmental effects associated
with, the proposed project. The operator
must provide geological information,
including the name and estimated tops
of all geologic groups, formations,
members, and zones. The operator must
also provide the estimated depths and
thickness of formations, members, or
zones potentially containing usable
water, oil, gas, or prospectively valuable
deposits of other minerals that the
operator expects to encounter, and their
plans for protecting such resources. The
BLM uses this information and the
BLM’s geologists’ and engineers’
professional reviews to ensure that
usable water zones are protected.
The operator must provide minimum
specifications for blowout prevention
equipment that they will use to keep
control of well pressures encountered
while drilling. The BLM evaluates the
proposed equipment to determine that it
is adequate for anticipated pressures
that the well may encounter in order to
prevent loss of control of the well and
potential environmental issues. The
operator must provide a proposed
casing program, including the size,
grade, weight, and setting depth of each
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casing string. The BLM engineers
evaluate the proposed casing to ensure
that it is being set at proper depths to
protect other resources, including
usable water. The BLM engineers also
ensure that the casing size and strength
is sufficient for the depths at which it
will be set, and the pressures that the
well will encounter.
The operator must provide
information regarding the proposed
cementing program. This includes the
amount and types of cement the
operator will use for each casing string,
and the expected top of cement for each
casing string. The cement is critical for
the isolation and protection of usable
water since it is the cement that
establishes a barrier outside the casing
between any hydrocarbon bearing zones
and usable water zones. The proposed
cementing program is the first step for
this protection. The BLM engineers
evaluate the proposed cementing
program to ensure that the volume and
strength of the cement is adequate to
achieve the desired protections.
The operator must include in the
drilling plan information regarding their
proposed drilling fluid. The operator
must provide the type and
characteristics of the proposed
circulating medium for drilling each
well bore section, including the
quantities and types of mud the operator
will maintain, and the monitoring
equipment the operator will utilize on
the circulating system. The BLM
engineers review this information to
ensure that the drilling fluid system and
additives will be compatible and not
detrimental to all usable water and
prospectively valuable mineral zones
that the well bore may encounter. The
operator must also provide their
proposed testing, logging, and coring
procedures. This may include
resistivity, gamma ray, spontaneous
potential, caliper, and neutron logs as
well as cement evaluation logs. The
BLM reviews the proposed logging suite
and determines if the operator will need
to run any additional logs to provide
additional downhole information.
The operator’s drilling plan must
address the expected bottom-hole
pressure and any anticipated abnormal
pressures, temperatures, or potential
hazards that the well may encounter.
Hazards may include lost circulation
zones, hydrogen sulfide zones, or faults
and fractures. The operator must also
include a plan for mitigating such
hazardous. The BLM geologists review
this information to determine if any
other anticipated hazards exist. The
BLM engineers review this information
to ensure the proposed mitigation to
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address any anticipated hazards is
adequate.
The operator must include in its
drilling plan any other information
regarding the proposed operation that it
would like the BLM to consider. This
might include, but is not limited to, the
directional drilling plan for deviated or
horizontal wells, which would provide
the proposed wellbore path. The BLM
engineers review the proposed
directional plan to ensure there will not
be any potential issues with existing
wells.
The operator’s APD must also include
a surface use plan of operations, or the
equivalent required by another surface
management agency. The surface use
plan must contain sufficient details of
the proposed surface use to provide for
safe operations, adequate protection of
the surface resources, groundwater, and
other environmental components. The
operator must also describe any Best
Management Practices (BMP) they plan
to use. BMPs are state-of-the-art
mitigation measures applied to oil and
natural gas drilling and production to
help ensure that operators conduct
energy development in an
environmentally responsible manner.
BMPs can protect water, wildlife, air
quality, or landscapes. The BLM
encourages operators to incorporate
BMPs into their plans.
The operator’s surface use plan
should follow the BLM’s Surface
Operating Standards and Guidelines for
Oil and Gas Exploration and
Development, which is commonly
referred to as The Gold Book.5 The BLM
developed The Gold Book to assist
operators by providing information on
the requirements for obtaining permit
approval and conducting
environmentally responsible oil and gas
operations.
The operator’s surface use plan must
include information regarding existing
roads they plan to use to access the
proposed well location and must
explain how they will improve or
maintain existing roads. The surface use
plan must also include the operator’s
plan for any new access roads they plan
to build. The operator must design roads
based upon the type of road, the safety
requirements, traffic characteristics,
environmental conditions, and the type
of vehicles that will use the road. The
proposed road description must
include: Road width, maximum grade,
crown design, turnouts, drainage and
ditch design, on-site and off-site erosion
5 The Gold Book is available on the BLM’s
website, at: https://www.blm.gov/programs/energyand-minerals/oil-and-gas/operations-andproduction/the-gold-book.
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control, revegetation of disturbed areas,
location and size of culverts and/or
bridges, fence cuts and/or cattleguards,
major cuts and fills, source and storage
of topsoil, and the type of surface
materials that the operator will use.
The operator must include a map
showing all known wells, regardless of
well status (producing, abandoned, etc.)
within a one-mile radius of the
proposed location. The BLM uses this
information to ensure the proposal does
not conflict with any current surface
use. The BLM uses this well information
to identify any potential downhole
conflicts or issues between the existing
wells and the proposed well. If the BLM
does identify conflicts, the BLM will
require the operator to modify their
proposal or to submit plans to mitigate
the issue.
The operator must include a map or
diagram that shows the location of all
production facilities and lines they will
install if the well is successful (i.e., a
producing well), as well as any existing
facilities. This would include all buried
oil, water, or gas pipelines and all
overhead and buried power lines. The
BLM reviews this information to
identify any potential conflicts with the
proposed facilities.
The operator must include in their
surface use plan information concerning
the water supply, such as rivers, creeks,
springs, lakes, ponds, and wells that the
operator plans to use for drilling the
well. This may or may not be the same
source of water the operator plans to use
for their hydraulic fracturing operations.
The BLM does not regulate water usage,
but the BLM does use the information
about water supply in conducting the
environmental analysis of the APD. The
BLM uses the information to determine
if the operator must obtain any
additional approvals such as a right-ofway across Federal lands that may be
necessary for the transport of water.
The operator must include a written
description of the methods and
locations it proposes for safe
containment and disposal of each type
of waste material (e.g., cuttings, garbage,
salts, chemicals, sewage, etc.) that
results from drilling the proposed well.
The narrative must include plans for the
eventual disposal of drilling fluids and
any produced oil or water recovered
during testing operations. The operator
must describe plans for the construction
and lining, if necessary, of the reserve
pit.
The surface use plan must include the
character, intended use, and source of
all construction materials, such as sand,
gravel, stone, and soil material. The
operator must identify the location and
construction method and materials from
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all anticipated ancillary facilities such
as camps, airstrips, and staging areas.
This information will be used to assess
the environmental impacts of the
proposed operations.
The operator must include a diagram
of the proposed well site layout. The
layout must show the location and
orientation of the following: The
proposed drill pad, the reserve pit/
blooie line/flare pit location, access road
entry points, and the reserve pit
showing all cuts and fills, the drilling
rig, any dikes and ditches to be
constructed, and topsoil and/or spoil
material stockpiles.
The operator must submit a plan for
the surface reclamation or stabilization
of all disturbed areas. The plan must
address interim (during production)
post-drilling reclamation for the area of
the well pad not needed for production,
as well as final abandonment of the
location. The plan must include, as
appropriate, the following:
Configuration of the reshaped
topography, drainage systems,
segregation of stockpiles, surface
disturbances, backfill requirements,
proposals for pit closures, redistribution
of topsoil, soil treatments, seeding or
other steps to reestablish vegetation,
weed control, and practices necessary to
reclaim all disturbed areas, including
any access roads and pipelines.
If the BLM does not manage the
surface, the surface management agency
must approve the surface use plan
according to their respective regulations
and guidance documents.
The APD must provide proof of
adequate bond coverage as required by
existing 43 CFR 3104.1 for Federal lands
and by 25 CFR 211.24, 212.24, and
225.30, for Indian lands. These
regulations require the operator or the
lessee to have an adequate bond in place
prior to the BLM’s approval of the APD.
If the BLM determines that the current
bond amount is not sufficient, the BLM
can require additional bond coverage.
The BLM determines the need for bond
increases by considering the operator’s
history of previous violations, the
location and depth of wells, the total
number of wells involved, the age and
production capability of the field, and
any unique or unusual conditions in the
planned drilling operations or in the
surrounding environment.
Upon receipt of a complete APD, the
BLM will schedule an onsite inspection
with the operator. The purpose of the
onsite inspection is for the BLM and
operator to further identify site-specific
resource concerns and requirements not
originally identified during the
application stage. Prior to, or in
conjunction with, the onsite inspection,
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the BLM or other surface management
agency will advise the operator if any
special inventories or studies are
required, such as for cultural resources
or threatened and endangered species.
The onsite inspection team will
include the BLM, a representative of any
other surface management agency, the
operator or permitting agent, and other
parties associated with planning work
on the project, such as the operator’s
principal dirtwork contractor, agency
resource specialists, surveyors, and
pipeline or utility company
representatives. When the onsite
inspection is on private surface, the
BLM will invite the surface owner to
attend. The purpose of the onsite
inspection is to discuss the proposal;
determine the best location for the well,
road, and facilities; identify site-specific
concerns and potential environmental
impacts associated with the proposal;
and discuss the conditions of approval
(COA) or possible environmental BMPs.
If the BLM identifies resource conflicts,
the BLM has the authority to require the
operator to move surface facilities to
locations that would reduce resource
impacts while still allowing
development of the leased minerals.
After the BLM has reviewed the
operator’s proposed plans and
conducted the onsite inspection, the
BLM will prepare an environmental
impacts analysis document in
conformance with the requirements of
NEPA, and the Department of the
Interior’s regulations. The extent of the
environmental analysis process and the
time period for issuance of a decision on
the APD will depend upon the
complexity of the proposed action and
resulting analysis, the significance of
the environmental effects disclosed, and
the completion of appropriate
consultation processes. In each case, the
environmental analysis considers
environmental concerns and resource
issues in the area, including those the
BLM or operator identified during the
onsite inspection, such as potentially
impacted cultural resources, endangered
species, surface water, ground water,
and other natural resources. A group of
resource specialists conduct the
analysis. The composition of the team
depends on the resource issues in that
area and any resource issues that the
BLM or operator identified during the
onsite inspection. The resource
specialists may include petroleum
engineers, geologists, natural resources
specialists, wildlife biologists,
archeologists, hydrologists, soil
scientists, botanists, recreation
specialists, range management
specialists, and realty specialists.
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The environmental analysis may be
conducted for a single well, a group of
wells, or for an entire field. The public
is welcome to provide input to the BLM
for inclusion in the analysis. The BLM
posts notices of all Federal APDs for
public inspection in the authorizing
office and on the internet. For large
projects, such as field development
environmental assessments or
environmental impact statements, the
BLM will go through public scoping and
will issue a draft analysis for public
comment prior to completing the final
analysis and issuing a decision.
The environmental analysis will
identify potential impacts from the
proposed action. The BLM will develop
any necessary COAs to mitigate those
potential impacts. If the BLM identifies
unacceptable impacts, the BLM will ask
the operator to modify its proposal, or
the BLM may deny the application. The
BLM will attach the COAs to the
approved APD. The operator must
follow the approved plan and all COAs.
Upon BLM’s approval of an APD, the
operator may commence drilling of the
well. In addition to the approved plan
and the COAs attached to the APD, the
operator must also comply with the
requirements of Onshore Order 2.
Onshore Order 2 details the BLM’s
uniform national minimum standards of
performance expected from operators
when conducting drilling operations on
Federal and Indian lands. Many of the
requirements of Onshore Order 2 ensure
the protection of usable water. Onshore
Order 2 defines ‘‘isolating’’ as ‘‘using
cement to protect, separate, or segregate
usable water and mineral resources’’
and ‘‘usable water’’ as ‘‘generally those
waters containing up to 10,000 ppm of
total dissolved solids.’’
Onshore Order 2 requires that the
operator conduct the proposed casing
and cementing programs as approved to
protect and/or isolate all usable water
zones, lost circulation zones,
abnormally pressured zones, and any
prospectively valuable deposits of
minerals. It requires that the operator
determine the casing setting depths
based on all relevant factors, including:
Presence/absence of hydrocarbons;
fracture gradients; usable water zones;
formation pressures; lost circulation
zones; other minerals; or other unusual
characteristics. It also requires the
operator to report all indications of
usable water.
Onshore Order 2 requires the operator
to run centralizers on the bottom 3
joints of surface casing to help ensure
the casing is centered in the drilled hole
prior to cementing. This helps to ensure
wellbore integrity. It also requires the
operator to cement the surface casing
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back to the surface either during the
primary cement job or by remedial
cementing. Cementing the surface
casing back to the surface ensures that
all usable water zones behind the
surface casing are isolated and
protected. Onshore Order 2 requires the
operator to wait until the cement for all
casing strings achieves a minimum of
500 psi compressive strength at the
casing shoe prior to drilling out the
casing shoe. It requires the operator to
use top plugs during cementing
operations to reduce contamination of
the cement by displacement fluid. It
requires the operator to use a bottom
plug or other acceptable technique, such
as a preflush fluid, inner string cement
method, etc., to help isolate the cement
from contamination by the mud fluid
being displaced ahead of the cement
slurry. By using proper cementing
techniques such as these, the operator
can complete the cement job as planned
and thus protect usable water.
Onshore Order 2 requires the operator
to pressure test the casing prior to
drilling out the casing shoe. This test
ensures the integrity of the casing.
Onshore Order 2 requires the operator to
conduct a pressure integrity test of each
casing shoe on all exploratory wells,
and on that portion of any well
approved for a 5000 psi blowout
preventer. The operator must conduct
this test before drilling 20 feet of new
hole. The pressure test ensures the
integrity of the cement around the
casing shoe.
Onshore Order 2 identifies the
minimum requirements for blowout
prevention equipment and the
minimum standards for testing the
equipment. Proper sizing, installation,
and testing of the blowout prevention
equipment ensures that the operator
maintains control of the well during the
drilling process, which is necessary for
protection of usable water zones.
The BLM conducts inspections of
drilling operations to ensure that
operators comply with the Onshore
Order 2 drilling regulations, the
approved APD, and the associated
COAs. The BLM drilling inspections
consist of two general types of
inspections: Technical and
environmental. The BLM petroleum
engineering technicians conduct
technical inspections of the drilling
operations, such as witnessing the
running and cementing of the casing,
witnessing the testing of the blowout
prevention equipment, and detailed
drilling rig inspections that include
review of documentation such as the
third party cementing job ticket, which
describes the cementing operation
including the type and amount of
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cement used, the cement pump
pressures, and the observation of
cement returns to the surface, if
applicable. Through witnessing the
operation or the review of the
documentation, the BLM inspectors
verify that the drilling operations are
conducted in accordance with the
approved plan and that no wellbore
issues exist. The BLM natural resource
specialists conduct environmental
inspections of drilling operations. The
environmental inspections focus
primarily on the surface use portion of
the approved APD. This includes
inspection of the access road, the well
pad, and any pits. While the BLM does
not have the budget or personnel
available to inspect every drilling
operation as it is occurring on Federal
and Indian minerals, the BLM conducts
inspections in accordance with an
annual strategy to ensure compliance
with the regulations, lease stipulations,
COAs for the plan, and permits.
As described above, the BLM has
numerous processes and requirements
to ensure that operators conduct oil and
gas exploration and development in an
environmentally responsible manner
that protects mineral and other
resources.
Within 30 days after the operator
completes a well, the operator is
required by Section IV(e) of Onshore
Order 1 to submit to the BLM a Well
Completion or Recompletion Report and
Log (Form 3160–4), which provides
drilling and completion information.
This includes the actual casing setting
depths and the amount of cement the
operator used in the well along with
information regarding the completion
interval, such as the top and bottom of
the formation, the perforated interval,
and the number and size of perforation
holes. The operator is required to
submit copies of all electric and
mechanical logs, including any cement
evaluation logs, which the operator ran
on the well prior to conducting
completion operations. The BLM
reviews this information to ensure that
the operator set the casing and pumped
the cement according to the approved
permit.
Once a well goes into production,
water is often produced with the oil and
gas. The produced water tends to be of
poor quality and is not generally
suitable for drinking, livestock, or other
uses without treatment and, therefore,
must be disposed of properly. Onshore
Oil and Gas Order 7 (Order 7) regulates
the disposal of produced water. Under
Onshore Order 7, operators must apply
to the BLM for authorization to dispose
of produced water by injecting the water
into a suitable formation, by storing it in
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pits, or by other methods approved by
the BLM. If the disposal is into injection
wells, the operator must obtain approval
under the Safe Drinking Water Act’s
Underground Injection Control (UIC)
program that is administered by the
Environmental Protection Agency
(EPA). In many states, the EPA has
granted primary enforcement authority
for the UIC program to the state agency
responsible for oil and gas development.
If the water will be stored in pits, the
BLM requires specific design standards
to ensure the water does not
contaminate the environment or pose a
threat to public health and safety.
After a well has been drilled and
completed, the BLM continues to
inspect the well until it has been
plugged and abandoned and the surface
has been rehabilitated. During the
production phase of the well, the BLM
inspections focus on two primary
issues: Production and the environment.
The Federal Government (for Federal
leases) or an Indian tribe or individual
Indian allottee (for Indian leases)
receives a royalty on the oil and gas
removed or sold from the lease based on
the volume, quality, and value of the oil
and gas. Royalties from Federal leases
are shared with the state as provided by
statute. Production inspections are done
to ensure the volume and quality of the
oil and gas is accurately measured and
properly reported. Environmental
inspections are done to ensure that well
pads and facilities are in compliance
with regulations, Onshore Orders, and
approved permits. Environmental
inspections include ensuring that pits
are properly constructed, maintained,
and protected from wildlife; identifying
leaking wells or pipelines; ensuring that
the wellsite and facilities are properly
maintained; and ensuring that proper
erosion controls and rehabilitation
measures are in place.
When a well has reached the end of
its economic life, Federal regulations
require it to be plugged and abandoned
to prevent oil and gas from leaking to
the surface or contaminating water
bearing zones or other mineral zones. 43
CFR 3162.3–4. Well abandonment can
be requested by the operator or required
by the BLM. In either case, the operator
must submit a proposal for well
plugging, including the length, location,
type of cement, and placement method
to be used for each plug. Onshore Order
2 contains minimum requirements for
well plugging. The operator must also
submit a plan to rehabilitate the surface
once the well has been plugged. The
goal of surface rehabilitation is to
remove obvious visual evidence of the
pad and to promote the long-term
stability of the site and vegetation.
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The BLM inspects both well plugging
and surface restoration. Well plugging
inspections are done to ensure the plugs
are set into the wellbore as approved by
the BLM. The inspector will witness the
depth and volume of cement used in
each plug as well as the physical
verification of the top of each plug.
When an operator has complete surface
restoration, it will notify the BLM. The
BLM will send surface protection
specialists to ensure the restoration is
adequate. Once the BLM is satisfied
with the restoration efforts, the BLM
will approve the operator’s Final
Abandonment Notice.
II. Discussion of the Final Rule and
Comments on the Proposed Rule
On July 25, 2017, the BLM proposed
to rescind the 2015 final rule because
we believed that rule was unnecessarily
duplicative of state and some tribal
regulations and imposed burdensome
reporting requirements and other
unjustified costs on the oil and gas
industry. The 60-day comment period
for that proposed rule (the 2017
proposed rule) ended on September 25,
2017 (82 FR 34464).
Discussion of Comments by Topic
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Water Quality
Many commenters state that the 2017
proposal, if finalized, will have negative
impacts on water quality and public
health. Commenters state that science
has shown that hydraulic fracturing can
be injurious to the natural landscape as
well as to human health and safety.
Commenters state that one danger from
hydraulic fracturing is contamination of
surface water by toxic chemicals that
leach off site. Another is that the fluids
may leak from the well into
underground aquifers. Commenters
assert that contamination on Federal
and tribal land runs off Federal lands
into the water systems that we use and
seeps into the groundwater we drink.
The BLM has reviewed incident
reports from Federal and Indian wells
since December 2014. This review
indicated that resource damage is
unlikely to increase by rescinding the
2015 rule because of the rarity of
adverse environmental impacts that
occurred from hydraulic fracturing
operations before the 2015 rule, and
after its promulgation while the 2015
rule was not in effect. The BLM believes
that the appropriate framework for
mitigating these impacts is through the
state regulations, through tribal exercise
of sovereignty, and through BLM’s own
pre-existing regulations and authorities
(pre-2015 final rule 43 CFR subpart
3162 and Onshore Orders 1, 2, and 7).
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The review and approval of the APDs
requires compliance with those existing
authorities and regulations to ensure
protection of the water resources, and
the local environment.
Multiple commenters claim that
hydraulic fracturing is a dangerous
practice that can contaminate our air
and water, while contributing to the
release of greenhouse gases. One
commenter states that, as the base of
scientific knowledge regarding risks
from hydraulic fracturing continues to
develop, the evidence continues to
build that hydraulic fracturing and shale
and tight gas development processes
pose a wide range of risks to human
health and the environment. Another
commenter asserts that no amount of
regulation can make hydraulic
fracturing safe, but that rescinding or
weakening the recently updated rules
only puts our shared resources at greater
risk. Further, the commenter states that
the updated rules are long overdue and
simply lay out basic standards to follow.
Commenters state that the 2015 rule was
enacted after years of review and should
not be weakened or repealed.
Commenters state that rescinding the
2015 rule would put our Federal lands
at risk by repealing our first line of
defense against groundwater
contamination.
The BLM initiated the development of
the hydraulic fracturing rule in 2010 in
response to public concerns. Relatively
few states had any regulations on
hydraulic fracturing at that time. In light
of this, a BLM regulation covering
wellbore integrity and usable water
protection seemed appropriate at that
time. Since promulgation of the 2015
rule, however, many states have
updated their regulations to address
hydraulic fracturing operations. The
BLM now believes that the 2015 rule is
duplicative of the states’ and some tribal
regulations, as well as some of the
BLM’s own pre-existing regulations and
authorities (pre-2015 rule 43 CFR
subpart 3162 and Onshore Orders 1, 2,
and 7), and is not necessary.
Some commenters are concerned that
hydraulic fracturing affects the
availability of water resources. These
commenters describe that once water is
used for hydraulic fracturing, it cannot
be returned to the water table and that
water is a precious resource that should
not be depleted in this fashion.
Recycling and reuse of flowback
fluids from ongoing hydraulic fracturing
operations is currently practiced in
many states, but the majority of
recovered fluids are still injected into
disposal wells regulated under the Safe
Drinking Water Act (SDWA). The 2015
rule, however, would not have
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mandated reuse or recycling. Therefore,
rescinding the 2015 rule will not affect
demands on water supplies or the reuse
or recycling of recovered fluids.
One commenter states that, although
incidents of contamination of
groundwater from hydraulic fracturing
are not frequent, due in part to
improvements in technology, they have
occurred in locations that raise concern
about the adequacy of protection. In
response to comments that list examples
of studies that find no linkages between
hydraulic fracturing and groundwater
contamination, one comment points to
the work of a former U.S. EPA scientist
linking hydraulic fracturing with
groundwater contamination. The
commenter adds that not all laboratory
tests have shown contamination of
groundwater in areas of hydraulic
fracturing because standard laboratory
tests do not always test for exotic,
highly water-soluble chemicals used in
hydraulic fracturing.
The referenced study suggested that
water wells in Pavillion, WY were
contaminated with hydraulic fracturing
wastes that had been stored in unlined
pits dug into the ground. The BLM has
several existing requirements, some of
which are set out at 43 CFR subpart
3162 and in Onshore Oil and Gas Orders
1, 2, and 7, that allow it to mitigate the
risks associated with oil and gas
operations, including any risks to
groundwater from hydraulic fracturing
operations. The BLM also possesses
discretionary authority allowing it to
impose site-specific protective measures
reducing the risks associated with
hydraulic fracturing. The BLM
Authorized Officers follow the BLM’s
regulations and authorities to review
and approve each APD. Operators also
must comply with existing state laws
and regulations and, on tribal lands,
tribal laws and regulations, including
those that are intended to prevent
groundwater contamination. The BLM
does not believe that the 2015 final rule
would reduce the risks of groundwater
contamination to an extent that would
justify the burdens imposed on
operators or the BLM by that rule.
One commenter states that the cost of
cleaning groundwater after it is
contaminated is exorbitant and therefore
that circumstances potentially causing
contamination should be avoided.
We agree. The BLM Authorized
Officers follow the BLM’s regulations
and authorities (pre-2015 rule 43 CFR
subpart 3162 and Onshore Orders 1, 2,
and 7) to review and approve each APD.
Operators also must comply with
existing state regulations, or, on tribal
lands, tribal laws. Those requirements
are intended to ensure protection of the
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water resources and prevent any
groundwater contamination. We are no
longer persuaded, though, that the 2015
rule would improve protection of
groundwater to an extent that would
justify the burdens on operators or the
BLM.
One commenter takes issue with the
statements in the 2017 proposed rule
that, ‘‘a review of incident reports from
Federal and Indian wells since
December 2014,’’ indicates that,
‘‘resource damage is unlikely to increase
by rescinding the 2015 final rule.’’ The
commenter asserts that the BLM
provides no support or explanation for
this statement and has failed to consider
many of the significant adverse
environmental impacts associated with
rescinding the 2015 rule.
The BLM did not find any increase in
the number of incidents related to
hydraulic fracturing completions in
BLM operations since December 2014.
The EPA study (EPA 2016) on hydraulic
fracturing was unable to identify any
specific activities of hydraulic fracturing
operations on Federal or Indian lands
that impacted the drinking water
resources, because the study did not
distinguish between hydraulic
fracturing on Federal or Indian lands
and hydraulic fracturing on other lands.
One commenter states that he has
lived in North Dakota for five years and
personally witnessed the purposeful
dumping of hydraulic fracturing water
along roads and ditches on the roads
leading to hydraulic fracturing sites.
The commenter states that most of the
oil and hydraulic fracturing waste spills
that happen on or near sites do not get
reported.
The 2015 rule did not address open
dumping of recovered fluids. Neither
the 2015 rule, nor this rule, alter the
requirement that permanent disposal of
produced water must be in accordance
with an approved plan. See Onshore Oil
and Gas Order No. 7, 58 FR 47354
(1993). Unpermitted dumping of
recovered fluids is outside the scope of
this rulemaking.
Multiple commenters assert that
BLM’s rescission of the 2015 rule is
appropriate because there has been no
proven case of groundwater
contamination from hydraulic fracturing
in the United States to date. Several
commenters state that studies developed
by the EPA and U.S. Geological Survey
(USGS) indicate that hydraulic
fracturing has not had an impact on
groundwater quality. One commenter
further states that several studies,
including an EPA study, a Yale
University study, and a study funded by
the Natural Resources Defense Council,
find no incidence of contamination of
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groundwater due to hydraulic
fracturing, which has been performed
on over 1.2 million wells since 1948.
Absent any confirmed instances of
hydraulic fracturing impacting
underground sources of drinking water,
a commenter asserts that there is no
protective advantage to the environment
from the 2015 rule.
The BLM generally agrees with the
commenter. We conclude that state and
some tribal regulations, in conjunction
with the BLM’s own pre-existing
regulations and authorities (pre-2015
rule 43 CFR subpart 3162 and Onshore
Orders 1, 2, and 7) have been effective
in ensuring protection of the water
resources and the local environment.
One commenter states that any
studies contained in the BLM’s original
administrative record that suggest that a
link exists between groundwater
contamination and oil and gas
production were focused on well
construction rather than hydraulic
fracturing as the cause of the
contamination. The commenter further
states the BLM and each of the states in
which Federal oil and gas is produced
had well construction rules prior to the
2015 rule, and that the BLM’s
administrative record does not provide
any evidence that a rule focused on
hydraulic fracturing would improve the
degree of protection related to well
construction.
The BLM agrees in part. Onshore Oil
and Gas Order No. 2 continues to apply
to the drilling and cementing of oil and
gas wells on Federal and Indian lands.
See 53 FR 46798 (1988). The 2015 rule
would have imposed additional
monitoring, testing, and reporting
requirements. In the preamble and
supporting documents for the 2015 rule,
though, the BLM cited a few instances
where surface or groundwater
contamination was caused by inter-well
communications during the hydraulic
fracturing operations. Those were not
directly linked to wellbore construction,
but rather caused by geologic fractures
and fissures which are prevalent in
some areas, or by lack of awareness of
other wellbores. However, the BLM also
possesses discretionary authority
allowing it to impose site-specific
protective measures that can be applied
when necessary to reduce the risks
associated with hydraulic fracturing.
One commenter noted that, in Federal
court, an oil company was found to
have caused permanent and irreparable
pollution of the Sac and Fox Nation’s
groundwater by oil and gas activities. As
a result of ineffective and absent
regulatory actions, portions of the Sac
and Fox Nation’s aquifer will be unsafe
to drink for generations.
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It appears that the operator in the
cited case did not follow the conditions
of the permit issued by the BLM for the
operation, and is responsible for the
damage. The BLM’s 2015 rule would not
have addressed such issues related to
violation of the rule on tribal lands and
neither would this rule.
One commenter describes that the
2015 rule would have redefined ‘‘usable
water,’’ modifying the term’s definition
to include ‘‘those waters containing up
to 10,000 parts per million (ppm) of
total dissolved solids.’’ The commenter
asserts a lack of any empirical evidence
or science-based support for a need to
protect water that is so saline that it can
kill livestock, and asserts that this
definition would expand the scope of
protected waters well beyond EPA’s
regulations under the Safe Drinking
Water Act.
Onshore Oil and Gas Order No. 2,
Section II. Y, states that ‘‘Usable Water
means generally those waters containing
up to 10,000 ppm of total dissolved
solids.’’ The BLM believes that the
standard set forth in Onshore Order No.
2 is appropriate and it will continue to
follow that standard.
Air Quality/Public Health
One commenter states that there are
unsafe levels of air pollution at every
stage of oil and gas development. Air
quality testing at hydraulic fracturing
sites in several states have revealed
levels of hydrogen sulfide and volatile
organic compounds capable of causing
respiratory, neurologic, and
cardiovascular disease, blood
dyscrasias, birth defects, and
malignancies after chronic and recurrent
exposure. The commenter claims that
we do not yet know the true level of risk
related to air contamination for workers,
neighboring families and communities.
The commenter asserts that flowback,
even when stored in closed tanks, can
liberate toxic volatile pollutants (such as
carcinogenic benzene) at very high
concentrations into the atmosphere. The
commenter states that workers should
be wearing respirator masks to minimize
serious health consequences.
In response to that comment, the BLM
notes that the 2015 rule would have
generally required recovered fluids to be
stored in tanks until a permanent
disposal plan was approved, but
allowed for exceptions and did not
require closed or vapor-recovery
systems. The 2015 rule was never
intended to be an air quality or
emissions regulation. Health effects
from air emissions and mitigation
measures were not addressed in the
2015 rule and are outside the scope of
this rule. Air quality and worker safety
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are regulated by other Federal, state, or
tribal agencies.
One commenter states that a new form
of hydraulic fracturing-related air
pollution may be increased levels of
indoor radon concentration (the number
one cause of lung cancer among nonsmokers) in homes located in areas
where hydraulic fracturing is used to
extract natural gas from shale
formations. The commenter highlights
that a peer-reviewed study published in
May 2015 by the National Institute of
Environmental Health Sciences,
‘‘Predictors of Indoor Radon
Concentrations in Pennsylvania, 1989–
2013,’’ documents a progressive upward
trend in ambient radon levels between
2005 and 2013 coincident with the
onset of hydraulic fracturing in
Pennsylvania. The commenter noted
that, at present, there are no state or
Federal regulations addressing this
newly discovered association.
In response to that comment, the BLM
notes that the 2015 rule did not address
radon concentrations, and rescinding
that rule will not affect radon
concentrations. Radon ‘‘association’’
with hydraulic fracturing operations is
outside the scope of this rulemaking.
One commenter states that unsafe
levels of air pollution found near
hydraulic fracturing sites are largely
ignored by Federal and state agencies.
The commenter suggest that, to remedy
this, monitoring of pollution emissions,
air testing of communities, and strict
standards to limit pollution are sorely
needed and should replace patchy,
inadequate state protections that do not
do enough to safeguard communities
that are increasingly exposed to the
deadly consequences of poorly
regulated hydraulic fracturing sprawl.
Another commenter states that diesel
emissions from heavy trucks and
machinery used during well site
preparation, drilling, and production
contain toxins and release diesel soot
particles, which increase health risks
including: Asthma attacks,
cardiopulmonary disease, respiratory
disease, pregnancy complications, and
premature death. In addition, the
commenter states that inhaling
respirable silica can cause silicosis and
lung cancer in miners, sandblasters, and
foundry workers. The commenter
further notes that, due in large part to
methane leakage and venting, the
greenhouse gas footprint of shale gas is
larger than the footprint of oil,
conventional gas, and even coal.
These comments are outside the scope
of the present rulemaking action.
Neither the 2015 rule nor this rescission
will cause air pollution, fugitive dust, or
greenhouse gas emissions to be greater
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or less. Air quality monitoring and
emissions standards are regulated by
other agencies.
In addition to air and water pollution,
one commenter expressed concern
about externalities of drilling
operations, such as noise pollution and
odors, which should be kept within
tolerance levels as drilling expands to
areas where more people live.
This comment is outside the scope of
this rulemaking because it addresses oil
and gas development in general and
fails to assert any specific alternative
approach or change from the 2017
proposed rule that the BLM should have
considered in this final rule with
respect to the regulation of hydraulic
fracturing operations on Federal and
Indian lands.
Chemical Disclosure
In this section, we describe the
comments the BLM received regarding
chemical disclosure and respond to
them all in the final paragraph of the
section.
Some commenters are concerned that
rescinding the 2015 rule will result in
chemicals used in the hydraulic
fracturing process not being disclosed
by operators. Commenters state that, as
the Federal lands managed by the BLM
are public lands, the public has a right
to clearly understand what is occurring
on them and any potential impacts that
those activities could have on water
resources. One commenter notes that a
recent study conducted by the Yale
School of Public Health found that, of
the compounds used in hydraulic
fracturing that they could identify and
study, 44 percent of the water pollutants
and 60 percent of air pollutants were
either confirmed or possible
carcinogens. Although these compounds
often make up only a small percentage
of the total volume of the fluid, many
are known to be toxic to humans at
levels as low as five parts per billion.
The commenter suggests that the 2015
rule would help to ensure proper
handling and would mitigate potential
exposure and impacts to public health
from hydraulic fracturing. Another
commenter describes a 2015 report
published by the EPA that stated that
well operators refused to disclose 11
percent of their ingredient records,
citing them as confidential business
information. Furthermore, one or more
ingredients in more than 70 percent of
disclosures were omitted, according to
the commenter.
One comment referred to a 2016
article entitled, ‘‘Hydraulic Fracturing
Chemicals Reporting: Analysis of
Available Data and recommendations
for Policy Makers,’’ which highlighted
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that 16.5 percent of chemicals used in
hydraulic fracturing between the years
2012 and 2015 were unreported.
One commenter expressed concern
regarding the BLM’s reliance on a third
party (FracFocus) to replace specific
transparency and public accountability.
In response to commenters on the 2015
rule, the BLM stated that, ‘‘compliance
with these rules will increase
transparency of the hydraulic fracturing
approval process and provide a means
for disclosure to the public of the fluids
utilized in the hydraulic fracturing
process.’’ The commenter complains
that the BLM now states that disclosure
of the chemical content of hydraulic
fracturing fluids to states or databases,
such as FracFocus, is more prevalent
than it was in 2015 and so there is no
need for a Federal chemical disclosure
requirement. The commenter asserts
that the slight shift in reporting
frameworks is insufficient justification
to remove regulations that promote
administrative transparency and public
disclosure of potentially harmful
chemicals. Furthermore, the commenter
stated that the BLM has yet to respond
to questions from the Secretary of
Energy’s Advisory Board raised in 2015
with respect to technical issues with
FracFocus, including a lack of
verification for data accuracy.
One commenter states that the BLM’s
analysis of state requirements for
chemical disclosure indicates that all
states reviewed require chemical
disclosure of hydraulic fracturing fluids
to FracFocus (with the possible
exception of New Mexico). The
commenter states that the BLM rule,
however, requires much more than just
disclosure of chemicals used in the
fracturing fluid. The commenter asserts
that California is the only state that has
equivalent requirements for each of the
elements that had been required in the
2015 rule and the only other state that
has any equivalent requirements is
Wyoming.
One commenter states that radioactive
substances are used in hydraulic
fracturing fluid to determine the
injection profile and location of
fractures created by hydraulic
fracturing. The commenter asserts that
these chemicals should be heavily
regulated as a matter of national security
and that all chemicals onsite should be
identified and reported by the operator.
The commenter states that the contents
of all materials and quantities injected
into the wells should be documented,
reported, and provided upon request.
The commenter states that polluters
should not remain unidentified because
the identifying features of the injected
slurry are protected as ‘‘trade secrets.’’
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Some commenters assert that it is not
burdensome to require the oil and gas
industry to disclose the chemicals they
are pumping into the ground in order to
extract petroleum.
In response to all of the foregoing
comments in this section, although we
agree that the information is readily
available to the operators or their
contractors, we are no longer convinced
that a BLM regulatory requirement
would improve access to that
information sufficiently to justify the
cost of compliance.
Most states with existing oil and gas
operations now have regulations that
require operators to disclose the
chemical content of hydraulic fracturing
fluids to either a publicly accessible
forum, such as FracFocus, state
regulatory agencies, or both. This
includes the States of California,
Colorado, Montana, New Mexico, North
Dakota, Oklahoma, Texas, Utah, and
Wyoming, which accounted for
approximately 99 percent of the total
well completions on Federal and Indian
lands from fiscal year (FY) 2010 to 2016.
In addition, there are 25 states that
currently use FracFocus for chemical
disclosures. These include seven states,
Colorado, Montana, New Mexico, North
Dakota, Oklahoma, Texas, and Utah,
with substantial BLM administered oil
and gas operations. The BLM now
believes that the disclosures of the
chemical content of hydraulic fracturing
fluids to state regulatory agencies and/
or databases, such as FracFocus is more
prevalent than it was in 2015 and that
there is no need for a duplicate Federal
chemical disclosure requirement, since
companies are already making those
disclosures on most of the operations,
either to comply with state law or
voluntarily. Furthermore, the 2015 rule
did not require disclosure of trade
secrets. See generally, 18 U.S.C. 1905;
43 CFR 3162.3–3(j) (2016). Therefore,
there is no reason to believe that
rescinding the 2015 rule will cause
operators to withhold more confidential
information about chemicals used in
hydraulic fracturing operations. To the
extent that the comments address
control of hazardous substances
generally, they are beyond the scope of
this rulemaking.
Earthquakes
Some commenters suggest that there
is a link between earthquakes and
hydraulic fracturing of rock formations.
One commenter states that significant
seismic activity is allowed without any
state or Federal constraints.
Commenters suggest a link between
hydraulic fracturing and wastewater
injection and earthquakes in Oklahoma
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and Ohio. Several commenters describe
a 2016 study that cautioned that
hydraulic fracturing in the United States
may be causing higher-than-recognized
induced earthquake activity that is
being masked by more abundant
wastewater-induced earthquakes. The
commenters assert that the injection of
oil and gas wastewater, often associated
with hydraulic fracturing, has been
linked to the dangerous proliferation of
earthquakes, including damaging
earthquakes in many parts of the
country.
In addition, one commenter asserts
that the hydraulic fracturing industry
has burdened tribal businesses and
homeowners that have to pay to repair
damages inflicted by these earthquakes.
The commenter asserts that induced
seismicity prevents tribal members from
access to Department of Housing and
Urban Development (HUD) funds for
home construction in areas that are now
unable to be adequately insured for
earthquake damage.
In response to the comments, U.S.
Geological Survey research indicates
that most induced seismicity has been
linked to wastewater injection, and
seldom to hydraulic fracturing
operations. While the 2015 rule contains
provisions regarding the storage of
recovered fluids, it did not include any
provisions regarding wastewater
disposal by underground injection,
which is regulated under the SDWA by
the EPA or an approved state or tribe.
The 2015 rule also did not change the
provisions of 43 CFR 3162.3–2 that
apply to injection activities. Pursuant to
Onshore Order 7, operators must submit
a wastewater disposal plan prior to
commencing operations, and they must
provide the BLM with a permit from the
EPA, state or tribe along with this plan.
Even if hydraulic fracturing operations
were found to cause damaging
seismicity, the 2015 rule would not
have controlled the effect, and,
therefore, rescinding that rule will not
increase the likelihood of seismicity
damage.
Rule Authorities
Commenters expressed a variety of
opinions about whether the BLM has
statutory authority to regulate hydraulic
fracturing operations on Federal and
Indian lands. This section of the
preamble first summarizes the
arguments for the BLM’s statutory
authority (and duty) and responds to
them. It next summarizes the arguments
against the BLM’s authority and
responds to them.
Some commenters assert that the BLM
has clear authority to regulate hydraulic
fracturing while other commenters
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disagree. More specifically, some
commenters state that the BLM issued
the 2015 rule as part of carrying out its
statutory duties to prevent unnecessary
or undue degradation of public lands
consistent with 43 U.S.C. 1732(b) and to
issue ‘‘comprehensive’’ regulations
‘‘necessary to implement the
provisions’’ of FLPMA, and to ‘‘carry
out the purposes of [FLPMA] and of
other laws applicable to the public
lands.’’ In addition, the commenters
state that, under the MLA, Congress
charged the BLM with ensuring that
Federal lessees conduct their operations
with ‘‘reasonable diligence, skill and
care,’’ and instructed the BLM to protect
the ‘‘interests of the United States’’ and
‘‘the public welfare.’’ The commenters
state that Congress authorized the BLM
to ‘‘prescribe necessary and proper rules
and regulations and to do any and all
things necessary to carry out and
accomplish the purposes’’ of the MLA.
These commenters conclude that the
2015 rule is consistent with the BLM’s
duties under FLPMA and MLA.
Similarly, some commenters state that
BLM lands are multiple use lands that
must fulfill not only resource
acquisition goals but public recreation
and public benefit goals. The
commenters state that actions must be
consistent with all the uses of BLM
property and the BLM cannot make this
determination without the information
requested in the 2015 rule. Some
commenters assert that activity on
public lands must be regulated
consistently across the nation,
especially when activities may affect the
ability of the BLM to uphold its
multiple use mandate. Some
commenters argue that the proposed
action indicates a preference for oil and
gas leasing and development over other
multiple uses. The commenters argue
that this mandate prohibits DOI from
managing public lands primarily for
energy development or in a manner that
unduly or unnecessarily degrades other
uses.
Some commenters state that the
proposed rescission rule is inconsistent
with the BLM’s statutory duties under
FLPMA, the MLA, and the IMLA. The
commenters state that the BLM
concluded in 2015 that the requirements
of the 2015 rule were necessary to meet
those obligations. The commenters
assert that the BLM’s proposed reversal
of the 2015 rule is not permissible under
FLPMA and other laws because the
BLM failed to explain its departures
from the factual conclusions it drew
when promulgating the rule in 2015.
Similarly, some commenters state that
it is a dereliction of duty to abdicate the
responsibility of management of the
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appropriate and proper use of public
lands to the states. Commenters state
that they rely on BLM oversight to
manage the use of these public lands for
the benefit of all Americans, not just the
profits of oil and natural gas companies.
Commenters assert that the 2017
proposed rule, if finalized, is guided by
the short term interests of a few at the
expense of long-term efforts to protect
our lands and most importantly, our
water.
We agree in part with the comments
in the previous four paragraphs. The
BLM’s actions related to oil and gas
operations on Federal land are subject to
FLPMA, MLA, the Mineral Leasing Act
for Acquired Lands (MLAAL), and other
statutes. FLPMA prescribes that the
public lands are to be managed for
multiple use and sustained yield, and
that the BLM is to prevent unnecessary
or undue degradation. The MLA
requires that Federal oil and gas leases
include provisions to ensure the
exercise of reasonable diligence, skill,
and care in operations. No court,
however, has held that FLPMA requires
BLM to manage each acre of public land
to support all uses at all times. Rather,
oil and gas operations are statutorily
authorized uses of the Federal lands,
and thus may be thought of as
‘‘necessary or due’’ degradation when
conducted according to appropriate
standards for protection of the lands and
associated resources.
With respect to legal duties, no statute
requires the BLM to regulate hydraulic
fracturing operations, and no statute
requires all oil and gas operations on
Federal lands to be subject to the same
regulations. (Indeed, lease stipulations
and COAs are often different in different
areas to address local conditions.)
Rather, the contents of operating
regulations are within the discretion of
the Secretary. Mineral Policy Ctr. v.
Norton, 292 F. Supp. 2d 30, 44–45
(D.D.C. 2003). State laws have always
applied to oil and gas operations on
public lands, even when those laws
differ from one another. Particularly
where, as here, there is no compelling
indication that modern state regulations
are allowing unnecessary or undue
degradation to the public lands, the
Secretary is within his discretion to
decide that rescinding the 2015 rule
would reduce the burdens both on
operators and the BLM, with little
reduction in the protection of those
lands.
This final rule represents no
dereliction of duty. See generally,
Gardner v. BLM, 638 F.3d 1217, 1222
(9th Cir. 2011). Furthermore, it has
nothing to do with decisions about
which Federal lands to open for leasing,
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or which parcels to be offered for lease.
Private, for-profit, development of oil
and gas on Federal lands is authorized
by the MLA, the MLAAL, and other
statutes, and thus objections to those
authorizations are outside the scope of
this rulemaking.
Other commenters assert that the BLM
lacked authority to issue the 2015 rule.
Some commenters argue that Congress
has not delegated authority to the BLM
to regulate hydraulic fracturing and has
granted only limited authority to the
EPA to regulate hydraulic fracturing
under the Safe Drinking Water Act
(SDWA). Another commenter states that
the BLM concedes that it cannot
regulate enhanced oil recovery, disposal
wells, or hydraulic fracturing using
diesel because Congress has designated
the EPA as the agency with regulatory
authority over those forms of
underground injection in the SDWA,
and the same conclusion should apply
with respect to non-diesel hydraulic
fracturing.
Some commenters argue that the 2015
final rule requirement to submit water
source and recovered fluid disposal
method encroaches upon state
jurisdiction over waters of the state and
over underground injection control
covered in the primacy agreement
between North Dakota and the EPA in
1983.
A commenter asserts that North
Dakota has a large number of ‘‘splitestate’’ tracts where the Federal
minerals have been severed from the
surface estate, which is owned by either
the State of North Dakota or private
parties. The commenter argues that the
2015 final rule inappropriately
broadened BLM’s authority to regulate
surface operations for hydraulically
fractured wells that penetrate Federal
minerals, but where the United States
does not own the surface.
With few exceptions, the arguments
described in the previous three
paragraphs were raised in the litigation
challenging the 2015 rule. We believe
that rescinding the 2015 rule alleviates
these concerns and, therefore, the BLM
need not address them here. The more
immediate point is that the BLM has
authority to rescind the 2015 rule, and
to restore the regulations existing prior
to the 2015 rule with the few exceptions
previously discussed. Those regulations
were promulgated in 1982 and amended
in 1988. See 43 CFR 3612.3–2 (2014); 47
FR 47765 (1982); 48 FR 36583 (1983); 52
FR 5391 (1987); 53 FR 17363 (1988); 53
FR 22847 (1988). No commenter
provided evidence that this rescission
would interfere with the regulation of
underground injections by states, tribes,
or the EPA under the SDWA (as
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amended). The BLM does not regulate
disposal wells; but BLM’s authorization
is required for use of BLM-managed
surface for a disposal well. Other
‘‘enhanced recovery’’ operations are also
outside the scope of this rulemaking.
Aside from ‘‘split estates’’ being
common in several states where the
BLM regulates oil and gas operations, no
commenter provided evidence that
rescission of the 2015 rule would be
‘‘inappropriate’’ as applied to splitestate lands. If after this rescission of the
2015 rule, the BLM needs to approve an
operation that would, for example,
require substantial quantities of water,
the requirements of NEPA and the
applicable regulations would apply.
One commenter states that, regardless
of the 2015 rule, the BLM already has
the ability to impose additional
conditions related to hydraulic
fracturing on operators. This includes
the authority to require the submission
of additional information in relation to
the permitting process as well as the
ability to require that specific actions be
taken by operators on-site to minimize
environmental impacts and ensure site
safety and security. The commenter
states that the agency has broad
authority to collect information. The
commenter also noted that, pursuant to
43 CFR 3160.0–9, the BLM may request
data so that proposed operations may be
approved or to enable the monitoring of
compliance with granted approvals, and
operators must respond to such requests
as a condition of Federal oil and gas
leases and as a precondition to issuance
of a permit to drill. Finally, the
commenter notes that the BLM also has
the authority to require operators to take
specific actions when developing a
lease.
The commenter is essentially correct.
After this rescission, the BLM will
continue to responsibly use its
authorities to carry out its duties under
the applicable statutes and regulations.
One commenter criticizes the BLM’s
intention to restore the regulations
under which prior approval is required
for ‘‘non-routine’’ hydraulic fracturing
operations. 43 CFR. 3162.3–2 (2014).
The commenter asserts that the BLM has
never treated the ‘‘fracturing’’ referred to
in 43 CFR. 3162.3–2 as equivalent to
hydraulic fracturing. The commenter
further argues that proponents of the
2015 rule have recognized that under 43
CFR. 3162.3–2 ‘‘companies generally
treated all hydraulic fracturing
operations as routine’’ and the BLM did
not exercise approval authority over
hydraulic fracturing.
In response to this and other similar
comments, the BLM reconsidered its
proposal to restore the regulatory text in
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43 CFR 3162.3–2(a) (2014) requiring
prior approval for ‘‘nonroutine
fracturing jobs.’’ As a result of this
review, the BLM decided not to restore
the ‘‘nonroutine fracturing’’ requirement
in this final rule.
As previously mentioned, prior to the
2015 rule, the regulations at 43 CFR
3162.3–2(a) (2014) provided in pertinent
part that a ‘‘proposal for further well
operations shall be submitted by the
operator on Form 3160–5 for approval
by the authorized officer prior to
commencing operations to . . . perform
nonroutine fracturing jobs. . . .’’ Those
regulations, however, did not define
‘‘nonroutine fracturing jobs’’ or provide
guidance to operators or the BLM
authorized officers on how to
distinguish ‘‘routine’’ from
‘‘nonroutine.’’
The BLM further notes that as a result
of considerable advances in oil and gas
development technology in the last 20
years, hydraulic fracturing practices that
would have been considered
‘‘nonroutine’’ when the BLM originally
issued the regulations requiring prior
approval for ‘‘nonroutine fracturing
jobs’’ are now commonly employed and
considered ‘‘routine.’’ The combination
of advances in oil and gas development
technology and the BLM’s existing
authority to mitigate the potential risks
of hydraulic fracturing operations
through site-specific protective
measures that are applied as a part of
the environmental review and approval
process at the APD stage has made postAPD approvals for ‘‘nonroutine
fracturing jobs’’ at most a very rare
occurrence. In fact, while the BLM has
not been tracking requests for approval
of ‘‘nonroutine fracturing jobs,’’ recent
inquiries to BLM state offices have not
revealed any examples of ‘‘nonroutine
fracturing’’ requests or approvals. Thus,
given that the ‘‘nonroutine fracturing’’
requirement has not, and will not
foreseeably serve any purpose, and that
removing it from the regulations could
reduce the potential for unproductive
confusion or paperwork without adverse
effects, the BLM has removed
‘‘nonroutine fracturing’’ from 43 CFR
3162.3–2(a) in this final rule.
As for whether the word ‘‘fracturing’’
in 43 CFR 3162.3–2 (2014), includes
hydraulic fracturing, both the plain
meaning and its use in the industry,
includes ‘‘hydraulic fracturing.’’ See,
e.g., Williams & Myers Manual of Oil
and Gas Terms, p. 420 (10th ed. 1997)
(quoting American Gas Ass’n, Glossary
for the Gas Industry (3d ed. 1981)). The
BLM has always interpreted that
regulation to include hydraulic
fracturing. The commenter does not
offer any other rational interpretation.
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Therefore, including ‘‘routine
fracturing’’ in the restored section
3162.3–2(b) makes plain that an
operator does not need the BLM’s prior
approval for hydraulic fracturing
operations, except those that involve
increased surface disturbance or that do
not conform to the standard of prudent
operating practice.
Adequacy of Existing Regulations and
Industry Practices
The following paragraphs summarize
comments regarding whether existing
regulations and industry practices are
adequate to protect public lands. We
first summarize and respond to
comments critical of the existing
regulations and industry practices, and
opposed to rescission of the 2015 rule.
Then we summarize and respond to
comments arguing that existing state
and Federal regulations and industry
practices provide adequate protection
for federal lands and associated
resources, and in favor of rescission of
the 2015 rule.
Multiple commenters state that when
the BLM rescinds the 2015 rule,
regulations would be as they existed
prior to adoption of the 2015 rule. One
commenter states that it is apparent that
almost no oversight of hydraulic
fracturing was required prior to the 2015
rule, however, and that the inadequacy
of the prior regulation for dealing with
issues related to hydraulic fracturing
was noted in the rulemaking process for
the development of the 2015 rule. The
commenter states that the prior
regulations required that the BLM
approve proposals for ‘‘further well
operations,’’ which included
‘‘nonroutine fracturing jobs’’ and eight
other activities. The commenter states
that no BLM approval was required for
‘‘routine fracturing’’ jobs unless there
was additional surface disturbance.
However, the commenter states that
‘‘nonroutine fracturing jobs’’ was not a
defined term and the BLM proposes to
continue to not define the term. The
commenter states that the lack of
defined distinction between nonroutine
hydraulic fracturing jobs and routine
hydraulic fracturing jobs made ‘‘this
distinction functionally difficult to
apply and confusing for both the agency
and those attempting to comply with the
regulations.’’ The commenter states that
the BLM therefore acknowledges that
almost all fracturing operations were
deemed routine and not requiring
approval from the BLM prior to
commencing operations. A separate
commenter notes that this ‘‘pre-existing
authority’’ clearly existed at the time the
2015 rule was promulgated and fails to
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provide a valid basis for the BLM’s
change in position.
Multiple commenters express concern
that state laws are insufficient to
regulate hydraulic fracturing activities.
The commenters state that, while some
states have requirements regarding
particular issues that are equivalent to
the 2015 rule, many gaps in regulation
remain. The commenters state that each
state has areas where its regulations are
weaker than the 2015 rule, and no state
requires the same best practices across
the board. The BLM should keep the
2015 rule in place to ensure consistent
protections across the dozens of states
with existing Federal oil and gas leases.
One commenter notes that, if the BLM
recognizes that certain states have less
comprehensive regulations and
enforcement mechanisms, it necessarily
concedes that the legal framework
within those states will not provide the
same protections as the regulations
promulgated by the 2015 rule and
therefore that the 2015 rule is not
duplicative of state regulations. Another
commenter offers that the 2015 rule
provided specific direction to states on
how to protect groundwater and other
resources and set forth a common
standard of environmental protection at
hydraulic fracturing sites and brought
together requirements for a set of
environmentally protective
requirements that could be easily
referenced in one place for consistent
implementation.
Multiple commenters argue that the
BLM’s analysis of state regulations
included in the RIA suggests the 2015
rule is not redundant. In particular, two
commenters highlight that the BLM, in
its discussion of the mechanical
integrity test requirement, states it ‘‘is
an industry recommended practice and
is required by almost all of the states
whose regulations we reviewed.’’ One
commenter states that the BLM rule
requires operators to perform a
successful mechanical integrity test
prior to fracturing at a test pressure
equal to that which will be applied
during the actual fracturing operation
and that the applied pressure must hold
for 30 minutes with no more than a 10
percent pressure loss. The commenter
states that only California and Montana
have rules that include these
requirements. The commenter states
that similar issues exist with regard to
the annulus pressure monitoring and
reporting provisions. The commenter
states further that, in its analysis of state
regulations for monitoring pressure
during hydraulic fracturing operations,
the BLM claims that all states reviewed,
other than New Mexico, Oklahoma, and
Utah, explicitly require monitoring
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during fracturing operations. The
commenter states that, as with state
mechanical integrity test rules, the mere
presence of a rule is not sufficient.
Rather, the commenter states, the
substance of state rules must be
analyzed to determine whether state
rules contain safeguards equivalent to
the BLM rule. In addition, with respect
to review of the storage tank
requirements, some commenters state
that the BLM acknowledges that
‘‘Although the use of tanks is reportedly
common, only 5 out of the 9 states in
our in-depth regulatory review had
requirements specifying that operators
must use tanks.’’
One commenter asserts that the fact
that all 32 states currently with Federal
oil and gas leases now have laws or
regulations that address hydraulic
fracturing operations in no way
indicates those regulations are sufficient
to fulfill the stipulations under
Executive Order 13783, Promoting
Energy Independence and Economic
Growth. Another commenter
highlighted that despite the existence of
state requirements, the BLM explained
in 2015 that ‘‘a major impetus for a
separate BLM rule is that states are not
legally required to meet the stewardship
standards that apply to public lands and
do not have trust responsibilities for
Indian lands under Federal laws.’’ 80 FR
16133; see id. at 16154. The commenters
assert that ‘‘an additional 12 states have
introduced laws or regulations’’
regarding hydraulic fracturing is a
natural consequence of the significant
public concern about the practice, but
does not obviate the need for Federal
regulatory standards that promote the
responsible development of public
lands and fulfill BLM’s own
independent statutory duties to ensure
that oil and gas operations on Federal
and Indian lands are performed in a
safe, responsible, and environmentally
protective manner.
One commenter states that, unlike
BLM’s 2015 rule, many states do not
require operators to obtain a permit
specifically for fracturing operations.
The commenter notes that, of the states
the BLM reviewed in the RIA, only
California, Montana, and Wyoming
require a permit for fracturing
operations. The commenter notes that
Oklahoma and Colorado require
notification before fracturing, while
New Mexico, North Dakota, Texas, and
Utah require neither a permit nor
advanced notification. The commenter
states that this is a significant difference
between state regulations and the 2015
rule.
One commenter specifically claims
that New Mexico is second only to
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Wyoming in the number of producing
oil and natural gas leases on federally
managed land, yet state regulations lack
important safeguards included in the
2015 rule. The commenter notes that,
for example, New Mexico’s hydraulic
fracturing regulations do not include
measures to prevent ‘‘frack hits,’’ which
occur when the hydraulic fracturing of
one well causes a pressure transfer that
interferes with production in another
well. The commenter states that, as
acknowledged in the EA for the
rescission of this rule, these frack hits
pose a tangible threat to water resources
and the ecological integrity of public
land subjected to excessive and
haphazard drilling.
One commenter contends that the
2015 rule contains two essential safety
components: Wellbore testing prior to
hydraulic fracturing and storage of
flowback waste in tanks rather than pits.
The commenter states that these two
areas, if not adequately regulated,
present significant risks of
environmental contamination. The
commenter asserts that the 2015 rule
represented improvements over existing
Federal and Colorado state rules in
these areas. The commenter states that,
in proposing to rescind them, the BLM
clearly recognized what researchers
have also concluded: Hydraulic
fracturing poses pollution risks to air,
soil and water that are highly correlated
with failure to ensure wellbore integrity
and pit storage of waste. The commenter
states that the 2015 rule is the BLM’s
best determination, based on its own
expertise and expert outside input, for
preventing such contamination and the
rule should therefore not be rescinded.
One commenter stated that BLM’s
suggestion that a major expansion of
state regulation has occurred since 2015
is misleading because the states with
new regulations represent an
insignificant fraction of Federal oil and
gas development.
One commenter states that the
Appendix to the EA for the proposed
rule showed that the new state
regulations lack many of the protections
imposed by the 2015 rule. The
commenter states that, for example,
most state regulations do not mandate
the use of tanks instead of open pits, do
not require measures to prevent frack
hits, and do not require the same
measures to ensure adequate cementing.
One commenter said that the BLM
assumes substantial continued use of
storage tanks by operators in many
states even after the rule is rescinded,
although this is implausible. The
commenter states that, for example, the
BLM assumes that 100 percent of
operators in Texas and New Mexico will
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61937
use tanks even after rescission because
of state regulations despite the fact that
both states allow exemptions to their
regulatory standards. The commenter
states that the BLM also assumes 100
percent voluntary compliance in Utah
despite the state’s ‘‘unclear’’ standards,
and 92 percent voluntary compliance in
Wyoming. The commenter states that
the estimation of voluntary compliance
rates is based partly on the fact that
‘‘tanks are likely to be less costly than
pits on smaller and medium volume
jobs.’’ The commenter states that
without a Federal regulatory backstop,
past voluntary compliance rates and
past evidence of job size in particular
states do not guarantee the continued
use of tanks in the future.
In response to the foregoing
paragraphs in this section, when issuing
the 2015 rule, the BLM acknowledged
that it already had ‘‘an extensive process
in place to ensure that operators
conduct oil and gas operations in an
environmentally sound manner that
protects resources’’ (80 FR 16133). At
that time, the BLM also noted that while
‘‘the regulations and Onshore Orders
that have been in place to this point
have served to provide reasonable
certainty of environmentally responsible
development of oil and gas resources
. . .,’’ the 2015 rule ‘‘will complement
these existing rules by providing further
assurance’’ that hydraulic fracturing
operations are conducted in an
environmentally responsible manner
across all public and Indian lands (id.
at 16137). However, as previously
noted, in accordance with Executive
Order 13783 and Secretarial Order No.
3349, the BLM recently conducted a
review of the 2015 rule, existing state
laws and regulations, existing Federal
authorities and recent incident reports
submitted to the BLM for Federal and
Indian oil and gas operations. As a
result of this review, the BLM now
believes that the 2015 rule imposes
unnecessary and unjustified compliance
costs and burdens. Moreover, in light of
state regulatory programs, the
sovereignty of tribes to regulate oil and
gas operations on their lands, and the
BLM’s pre-existing regulations and
Onshore Oil and Gas Orders and other
Federal authorities, the rescission of the
2015 rule will not lead to poorly
regulated oil and gas development
activities, including hydraulic fracturing
operations, on Federal and Indian lands.
State regulatory programs can more
readily address local conditions than
may the BLM’s rules. Thus, the fact that
state rules differ from each other and are
not identical to the 2015 rule do not
render state programs ineffective, or the
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2015 rule essential. Furthermore, as
expressed in the Executive Orders, it is
this Administration’s policy to reduce
unnecessary regulatory burdens on
energy development. Based on the rarity
of adverse environmental impacts that
have occurred from hydraulic fracturing
operations before the 2015 rule, and the
lack of compelling evidence that state
regulatory programs are inadequate, the
2015 rule is a duplicative layer of
Federal regulation that should be
rescinded. To the extent that the
comments address the pre-2015 rule
requirements for prior approval of
‘‘nonroutine fracturing jobs,’’ see the
BLM’s response to comments in the
Rule Authorities section above. As
previously discussed, the BLM has
decided not to restore the requirements
for ‘‘nonroutine fracturing jobs’’ in 43
CFR 3162.3–2(a).
One commenter states that the
proposed rescission of the 2015 rule
does not provide substantive evidence
that industry practice is sufficient to
prevent the pollution and degradation of
hydrological resources on public lands.
The commenter states that, given its
self-described mandate to provide bona
fide minimum standards to ensure
industry compliance, as well as its
obligations under NEPA, the BLM
should not rescind protections given to
groundwater in the 2015 Rule.
While industry practices can and
often do work to appreciably reduce the
risks associated with oil and gas
development, the BLM does not solely
rely on industry practice to ensure that
oil and gas development operations on
public lands are conducted in an
environmentally responsible manner.
Operators on Federal lands must
comply with all Federal, state, and local
requirements. On Indian lands, they
must comply with all Federal and tribal
permitting and reporting requirements.
As previously noted, the BLM has an
extensive process in place to ensure that
operators conduct oil and gas operations
in a safe and environmentally sound
manner that protects resources. The
environmental reviews conducted under
NEPA provide an opportunity for the
BLM to consider and mitigate
potentially adverse environmental
impacts, including those involving
hydrological resources. If hydrological
concerns arise during the BLM’s review
of a specific oil and gas proposal, the
BLM may require additional
information, or impose protective
measures, such as lease stipulations or
COAs attached to APDs, to mitigate the
potential adverse impacts.
One comment disapproves of the
proposed rescission because of a lack of
reasonable regulation in Idaho to protect
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the communities impacted by hydraulic
fracturing. The commenter adds that
there is a lack of standardization in
incident reporting processes in different
states by highlighting a peer-reviewed
study published in February 2017 in the
Journal of American Chemical Society
entitled, ‘‘Unconventional Oil and Gas
Spills: Risks, Mitigation Priorities, and
State Reporting Requirements.’’ The
study points out differences in reporting
requirements in each of the four states
that produce most oil and gas using
hydraulic fracturing, and documents a
total of 6,648 spills between 2005 and
2014.
Contrary to the commenter’s
assertion, the BLM reviewed the
applicable Idaho state laws and
regulations and found an extensive
regulatory framework for addressing the
risks associated with hydraulic
fracturing. See Idaho Admin. Code
§§ 20.07.02.210 and 20.07.02.211. As
previously discussed, the fact that state
regulatory programs differ from each
other and are not identical to the 2015
rule does not render the state programs
ineffective, or the 2015 rule essential.
Furthermore, operators on Federal or
Indian lands are required to report
adverse incidents directly to the BLM.
The BLM requires operators to clean up
spills promptly and thoroughly. Those
requirements will not change with the
rescission of the 2015 rule.
Multiple commenters asserted that the
hydraulic fracturing regulations of
specific states are adequate, and thus
the 2015 rule is not needed. One
commenter highlighted that there has
never been a mechanical failure in
North Dakota since the North Dakota
Industrial Commission’s hydraulic
fracturing regulations were
implemented; a separate commenter
asserts that the regulatory oversight
provided by the State of North Dakota
protects the environment while
providing permitting in a careful but
timely manner. Another commenter
suggested that, in Wyoming, operators
have employed hydraulic fracturing
technology safely and efficiently for
decades. Another commenter asserts
that New Mexico’s hydraulic fracturing
rules and regulations are protective of
the environment and that hydraulic
fracturing is proficiently regulated by
the State of New Mexico, including
rigorous protocols for casing, cementing,
completions, recompletions and all
associated procedures, including
extensive monitoring and pressuretesting requirements, as well as
mechanical and pressure-based well
integrity testing. That commenter states
that adding an additional layer of
Federal regulation on top of an efficient
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and effective set of existing state
regulations will provide no additional
environmental protection. Additionally,
one commenter states that the State of
Utah has an effective regulatory program
that, for many years, has successfully
monitored the construction and
operation of oil and gas wells, including
well completion operations, such as
hydraulic fracturing, water
management, and chemical disclosure.
Another commenter also asserts that
Colorado rules and regulations along
with the Memorandum of Agreement
with the BLM (and the United States
Forest Service) for Permitting of Oil and
Gas Operations on BLM and National
Forest Service Lands in Colorado should
suffice in coordinating the permitting of
oil and gas operations on Federal lands.
One commenter states that, in
Oklahoma, regulators live in the
communities most affected, are in touch
with evolving technical and scientific
data, and have a demonstrated track
record of working effectively with
industry as well as the other
stakeholders of public and private
lands. In addition, a commenter asserts
that Western States with oil and gas
production have robust regulations to
protect the environment and public
health and are best-equipped to regulate
oil and gas development. The
commenter asserts that the Western
States have experienced few, if any,
adverse impacts involving water quality
and water allocation attributable to
hydraulic fracturing and that the
process has been used for more than a
million wells for over sixty years, and
is responsible for increasing the nation’s
ability to recover oil and gas at great
economic benefit.
The BLM thanks the commenters for
providing comments and supporting
information.
One commenter states that the EA for
the 2017 proposed rule reveals that
misguided public sentiment regarding
hydraulic fracturing was a lead
motivator for the BLM’s initiation of
rulemaking in 2010. The commenter
states that BLM also accurately observed
that adverse environmental impacts
from hydraulic fracturing were a rare
occurrence prior to the final 2015 rule,
and that observation remains true today.
The commenter asserts that, instead of
imposing a costly regulatory burden on
oil and gas operators, the BLM would be
better served by dedicating resources to
countering these unfounded public
concerns.
The BLM agrees that the 2015 rule
imposes compliance costs on the oil and
gas industry that are no longer justified.
The remaining statements in this
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comment are outside the scope of this
rulemaking.
One commenter states that the 2015
rule would have required that all fluids
recovered between the commencement
of hydraulic fracturing operations and
the authorized officer’s approval of a
produced water disposal plan under
BLM requirements must be stored in
rigid enclosed, covered, or netted and
screened above-ground tanks. The
commenter further states that no
regulatory mechanism exists for the
‘‘approval of a produced water disposal
plan’’ on an individual well basis, thus
the limitations the 2015 rule purports to
apply to recovered fluids storage are
premised on an administrative approval
process that does not exist.
As this final rule rescinds the 2015
rule, this comment is outside the scope
of the present rulemaking action.
Adequacy of Tribal Regulations
Multiple commenters state that the
BLM’s suggestion that the 2015 rule is
‘‘duplicative’’ of existing tribal
regulation is unsupported. The
commenters state that the differences
between the 2015 BLM rule and other
regulations are even greater on Indian
lands, where many tribes have not
developed their own regulatory
programs to manage hydraulicallyfractured oil and gas development. The
commenters state that this is
acknowledged in the EA. Another
commenter asserts that relying on state
regulations is inadequate for protecting
tribes. One commenter describes
experiencing multiple oil spills related
to injection wells on tribal lands and the
lack of resources to respond and hold
corporations accountable for the injury,
damage, and unnecessary burden the oil
industry placed on the tribe and its
resources. The commenter states that,
even though the sovereignty of tribes to
regulate operations on their lands may
be an option and reality for some tribes,
others have yet to develop the capacity
to enforce such regulations on their
lands and may never have the resources
to effectively manage and enforce oil
and gas regulations. The 2015 rule
would directly benefit and help protect
these tribes.
We acknowledge that not all oil and
gas producing tribes have exercised
their sovereignty to regulate hydraulic
fracturing activities. Rescission of the
2015 rule, however, does not affect
those tribes’ options for promulgating
and implementing programs in exercise
of their self-governance and sovereignty.
In addition, the BLM regulations
applicable to tribal lands, which include
the regulations at 43 CFR subpart 3162,
as amended by this final rule, and
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Onshore Oil and Gas Orders 1, 2, and 7,
reduce the risks associated with
hydraulic fracturing by providing
specific requirements for well
permitting; construction, casing, and
cementing; and disposal of produced
water. These BLM regulations, along
with the enforcement mechanisms that
are available to the BLM on tribal lands,
provide reasonable assurance that oil
and gas development on tribal lands
will occur in an environmentally
responsible manner, even when tribal
regulations or enforcement mechanisms
to ensure responsible oil and gas
development are not fully developed.
Rule Process
Multiple commenters assert that the
BLM has failed to explain why the 2015
rule is no longer needed to ensure the
environmentally responsible
development of Federal oil and gas
resources. These commenters note that
the Supreme Court has outlined
procedures that an agency must take to
comply with the Administrative
Procedure Act (APA) when changing an
existing regulation, including the need
to provide a reasoned analysis or
reasoned explanation for the change.
The commenters contend that the BLM’s
2017 proposed rule does not meet these
requirements and is fraught with loose
language that does not demonstrate a
reasoned basis or reasoned explanation
for the change.
Some commenters assert that the
BLM’s decision to rely on Executive
Order 13783 and Secretarial Order 3349
to justify the proposed rescission fails to
provide the ‘‘reasoned explanation’’
required by the APA. These commenters
note that Executive Order 13783 directs
agencies to review regulations that
‘‘unduly burden the development of
domestic energy resources beyond the
degree necessary to protect the public
interest or otherwise comply with the
law.’’ They contend that the BLM does
not explain why the 2015 rule
‘‘burdens’’ the development of energy
resources as defined by the Executive
Order, particularly in light of the BLM’s
findings that the 2015 rule would cost
just a small fraction of a percent of the
profit margins of small operations. The
commenters further state that the
proposed rescission does not address
other provisions of the Executive Order,
including that ‘‘all agencies should take
appropriate actions to promote clean air
and clean water for the American
people.’’
Finally, some commenters state that
the BLM articulated a reasoned
justification in 2015 for the storage tank
requirement, and that the agency now
proposes to rescind that same
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requirement without addressing the
evidence from the 2015 record or
offering any explanation for why a tank
requirement would no longer deliver
important environmental benefits.
On the contrary, the BLM believes
that it has articulated a reasoned
justification for rescinding the 2015
final rule. It therefore has not changed
this final rule based on these comments.
The Supreme Court has explained that
‘‘[a]gencies are free to change their
existing policies as long as they provide
a reasoned explanation for the change,’’
‘‘display awareness that [they are]
changing position,’’ and ‘‘show that
there are good reasons for the new
policy.’’ Encino Motorcars, LLC v.
Navarro, __U.S. __, 136 S. Ct. 2117,
2125–26 (2016). However, agencies do
not need to show ‘‘that the reasons for
the new policy are better than the
reasons for the old one’’ or necessarily
‘‘provide a more detailed justification
than what would suffice for a new
policy created on a blank slate.’’ FCC v.
Fox Television Stations, Inc., 556 U.S.
502, 515 (2009).
The BLM has provided a reasoned
explanation for rescinding the 2015 rule
that accords with these requirements:
The BLM believes that the 2015 rule,
which would impose compliance costs
and information requirements that are
duplicative of regulatory programs of
many states and some tribes, is
redundant and therefore unnecessarily
burdensome on regulated entities. Any
marginal benefits provided by the 2015
rule do not outweigh the rule’s costs,
even if those costs are a small
percentage of the cost of a well. In fact,
benefits were largely unquantified in the
2015 rule. The BLM has also provided
good reasons for its new policy,
explaining that state regulatory
programs (including those of the states
with most of the Federal oil and gas
leasing), the sovereignty of tribes to
regulate operations on their lands, and
other preexisting Federal regulations
provide a better framework than the
2015 rule for mitigating the impacts
associated with hydraulic fracturing
operations. For example, there are
currently laws or regulations to address
hydraulic fracturing in all 32 of the
states in which the BLM currently
manages oil and gas leases, and the BLM
has several existing requirements, some
of which are set out at 43 CFR 3162.3–
1 and in Onshore Oil and Gas Orders 1,
2, and 7, that allow it to reduce the risks
associated with hydraulic fracturing.
Additionally, the BLM has explained
that rescinding the 2015 rule’s storage
tank requirement may alleviate some
on-the-ground indirect impacts, such as
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those associated with truck traffic to
transport tanks to and from well sites.
The BLM is not required to
demonstrate that its reasons for
rescinding the 2015 rule are better than
or refute its rationale for initially
promulgating the 2015 rule. This is
especially true where, as here, the 2015
rule was never operational and did not
engender serious reliance interests on
the part of the regulated community. By
providing an explanation for why it is
rescinding the 2015 rule and
demonstrating that there are good
reasons for relying on state regulations,
tribal sovereignty, and the BLM’s
preexisting regulations, the BLM has
provided the necessary justification for
changing its policy regarding the
regulation of hydraulic fracturing.
Furthermore, there is no legal
impediment to this Administration
implementing its policies and priorities
through rulemaking to rescind or amend
existing regulations.
Some commenters state that the BLM
failed to consider a full range of
alternatives in its environmental
assessment. In particular, the
commenters state that the BLM should
have analyzed alternatives that
strengthen the rule instead of rescinding
it, including alternatives that regulate
stimulation operations broadly, area of
review, strengthen frack hit protections,
baseline water testing, well
construction, and restricted chemicals.
The BLM disagrees. The BLM
considered a reasonable range of
alternatives in its environmental
assessment in light of the proposed
action’s purpose and need and the
environmental effects that may result
from rescinding the 2015 final rule.
NEPA requires an agency to analyze all
reasonable alternatives related to the
purposes of the agency’s action. Where,
as here, an agency prepares an EA, the
range of alternatives that the agency
must consider, and the degree of
analysis that is required, is less than is
required for environmental impact
statements. Moreover, ‘‘‘the range of
alternatives that [an] agency must
consider [in an EA] decreases as the
proposed action’s environmental impact
becomes less and less substantial,’ ’’
Earth Island Inst. v. United States Forest
Serv., 697 F.3d 1010, 1023 (9th Cir.
2012) (quoting Louisiana Crawfish
Producers Ass’n–West v. U.S. Army
Corps of Engineers, 463 F.3d 352, 356–
57 (5th Cir. 2006) (alterations omitted)),
and it becomes even more diminished
where, as here, an agency concludes
that the action being considered will
have a minimal environmental effect.
See Save Our Cumberland Mts. v.
Kempthorne, 453 F.3d 334, 342–43 (6th
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Cir. 2006). Furthermore, although the
unsigned draft EA accompanying the
proposed rulemaking analyzed only two
alternatives, the signed EA for this final
rule analyzes four alternatives, and
explains why other alternatives were
considered but not carried forward for
analysis.
As described in detail above, this final
rule will have minimal environmental
effects. It will not authorize hydraulic
fracturing operations as a whole, it will
not authorize any particular hydraulic
fracturing operation on Federal or
Indian lands, and it will not impact the
overall number of hydraulic fracturing
operations on Federal or Indian lands.
What few impacts may result from the
final rule will be mitigated by state and
tribal regulations and the preexisting
Federal regulations. In light of these
minimal impacts, the BLM did not need
to analyze additional alternatives
beyond the alternative that were
analyzed in the EA that has been
prepared for this final rule.
Additionally, the commenters are
mistaken that the BLM should have
analyzed alternatives that strengthened
the 2015 final rule. The purpose and
need of a proposed action determines
the universe of alternatives that an
agency must consider. The purpose of
the BLM’s proposed action (the 2017
prosed rule) ‘‘is to reduce and eliminate
unnecessary regulatory requirements in
order to more efficiently manage oil and
gas operations,’’ and the need is ‘‘to
more prudently balance the BLM’s
interest in mitigating the risks of oil and
gas development operations, including
hydraulic fracturing, . . . with the
compliance burdens it imposes on the
oil and gas industry.’’ Alternatives that
would retain or increase the regulatory
burdens imposed by the 2015 final rule
on the oil and gas industry would not
further the BLM’s purpose and need for
action and, therefore, did not have to be
analyzed.
Some commenters assert that the
BLM’s proposed rescission of the 2015
rule fails to comply with NEPA. These
commenters state that the EA prepared
by the BLM contains only a brief
discussion of a few of the impacts
related to groundwater, surface water,
and greenhouse gas emissions, which it
determines to be insignificant. The
commenters contend that these
determinations contradict those found
in the EA that the BLM prepared when
it promulgated the 2015 rule, ignore
recent science regarding hydraulic
fracturing, and contradict several
reviews of hydraulic fracturing
conducted in California and elsewhere
that demonstrate the potential for other
significant environmental impacts that
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may result from the repeal of the 2015
rule.
The BLM disagrees with the
commenters that the EA’s discussion of
impacts constituted a NEPA violation.
Pursuant to CEQ’s regulations
implementing NEPA, an EA needs to
include only ‘‘brief discussions . . . of
the environmental impacts of the
proposed action and alternatives.’’ (See
40 CFR 1508.9(b).) The EA’s discussion
of the impacts related to groundwater,
surface water, and greenhouse gas
emissions satisfies this requirement.
Moreover, BLM notes that the EA
references appropriate portions of the
2015 EA addressing these impacts,
incorporating them into this EA.
Similarly, the BLM disagrees with the
commenters that its determinations that
the impacts to groundwater, surface
water, and greenhouse gas emissions of
this final rule are insignificant
contradict its determinations in the EA
prepared for the 2015 rule. With regard
to surface water and groundwater, the
2015 EA merely stated that, under the
No Action Alternative (i.e., existing
regulations), the impacts to surface
water and groundwater described in the
EA would be ongoing. The 2015 EA
neither stated nor concluded that the
impacts to those resources from the No
Action alternative would be significant.
Similarly, there is no contradiction
between the two EAs regarding impacts
related to greenhouse gas emissions.
The 2015 EA did not, as the commenters
suggest, determine that greenhouse gas
emissions related to the No Action
alternative would be significant. On the
contrary, the 2015 EA found that
although ‘‘the various action
alternatives would result in some small
variations in [greenhouse gas
emissions],’’ none of them ‘‘would
appreciably affect the amount of GHG
emissions arising from oil and gas
operations on Federal and tribal lands
as compared to [existing regulations].’’
This finding is consistent with the
BLM’s current determination that
rescinding the 2015 final rule would not
result in an appreciable increase in
greenhouse gas emissions.
The BLM also disagrees that the
determinations in the EA ignores recent
science regarding hydraulic fracturing.
The BLM reviewed and considered a
wide range of scientific evidence,
including recent studies, in assessing
the environmental impacts associated
with rescinding the 2015 final rule. For
example, the BLM gave considerable
weight to the EPA’s December 2016
study of hydraulic fracturing’s potential
impact on drinking water resources.
NEPA, however, does not require the
BLM to rely equally on all such studies.
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Rather, NEPA permits agencies to rely
on their expertise to determine which
studies are particularly relevant or
scientifically accurate. The fact that the
EA does not specifically address the
findings in the studies referenced in the
comment does not mean that such
studies were not considered. It simply
means that, in analyzing the impacts
associated with rescinding the 2015
final rule, the BLM found other studies
more relevant.
Some commenters assert that the BLM
violated NEPA by basing its EA on
unfounded assumptions rather than
sufficient evidence or analysis. The
commenter states, for example, while
acknowledging potential risks from the
impacts that it did consider, the BLM
finds that existing state and tribal
regulations and the BLM’s existing
authorities will ‘‘allow it to reduce the
risks associated with hydraulic
fracturing.’’ However, the commenter
states, the 2015 final rule remains more
comprehensive than the requirements in
many states and tribes, and the BLM has
previously stated that the final rule
‘‘would result in a reduction of the risks
associated with hydraulic fracturing
operations on Federal and Indian
lands.’’
The commenters are mistaken. The
BLM based its EA on evidence, analysis,
and technical expertise, not unfounded
assumptions. For example, the specific
conclusion referenced by the
commenters that existing regulatory
frameworks will allow the BLM to
reduce the risks associated with
hydraulic fracturing is based on the
BLM’s detailed review of state, tribal,
and Federal regulations. See RIA at
§ 2.12, and EA at Appendix 1. That
review indicated that all 32 states with
existing Federal oil and gas leases
currently have regulations to address
hydraulic fracturing operations, as do
some tribes with oil and gas resources.
Additionally, the BLM has several
existing requirements, some of which
are set out at 43 CFR subpart 3162 and
in Onshore Oil and Gas Orders 1, 2, and
7, that allow it to reduce the risks
associated with oil and gas operations,
including those of hydraulic fracturing.
The BLM also possesses discretionary
authority allowing it to impose sitespecific protective measures reducing
the risks associated with hydraulic
fracturing. Relying on this evidence to
conclude that the 2015 final rule was
duplicative of an existing regulatory
framework that will reduce the risks
associated with hydraulic fracturing
operations is a technical judgment
within the BLM’s area of expertise. The
BLM may rely on the judgment of its
own experts, see San Juan Citizens
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Alliance v. Stiles, 654 F.3d 1038, 1057
(10th Cir. 2011), even if the same
regulatory framework would have led
the commenters to arrive at a different
conclusion. See Greater Yellowstone
Coal. v. Flowers, 359 F.3d 1257, 1271 n.
14 (10th Cir. 2004).
The commenters are also mistaken
that the 2015 rule’s potential to reduce
risks somehow calls into question the
BLM’s conclusion that it can rely on
state, tribal, and Federal regulatory
framework to reduce the risks associated
with hydraulic fracturing operations.
The 2015 rule was meant to ‘‘add to’’
and ‘‘complement’’ this existing
regulatory framework. (80 FR 16128).
Regardless of whether those additions
would have resulted in additional risk
reductions, the BLM’s conclusion that
the existing regulatory framework is
capable of reducing risks remains valid.
Some commenters assert that the BLM
must prepare a full EIS before
rescinding the 2015 rule.
The BLM has not prepared an EIS in
response to those comments. NEPA
requires an agency to prepare an EIS
when it proposes to take a major Federal
action that significantly affects the
quality of the human environment.
Agencies must consider the context of
the action and the intensity of its
impacts to determine whether an action
significantly affects the quality of the
environment. As discussed in the BLM’s
EA and FONSI, the BLM considered the
context of rescinding the 2015 rule and
determined that doing so would remove
information requirements that are
duplicative of the regulatory programs
of many states and some tribes with
active oil and gas development. The
BLM also considered the intensity, as
that term is defined in CEQ’s NEPA
regulations, of rescinding the 2015 final
rule. Applying the intensity factors
listed in 40 CFR 1508.27(b), the BLM
determined that rescinding the 2015
rule would not have a severe impact on
the quality of the human environment.
Based on its considerations of the
context and intensity of the proposed
action, the BLM determined that
rescinding the 2015 rule will not
significantly affect the quality of the
human environment. In light of that
determination, it is unnecessary to
prepare a full EIS before rescinding the
2015 rule.
Some commenters assert that the BLM
failed to analyze indirect and
cumulative impacts of rescinding the
2015 rule.
Agencies are required to analyze the
indirect and cumulative impacts
associated with a proposed action. The
BLM’s analysis of those impacts is set
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61941
forth, respectively, in sections 4.0 and
5.0 of the EA.
One commenter states that ESA and
NHPA consultations are required before
the 2015 final rule can be rescinded.
The ESA requires an agency to
consult with the U.S. Fish and Wildlife
Service or National Marine Fisheries
Service to ensure that any action it
authorizes, funds, or carries out is not
likely to jeopardize the continued
existence of any listed species or result
in the destruction or adverse
modification of critical habitat. Section
106 of the NHPA requires Federal
agencies to take into account the effects
of their undertakings on historic
properties included on or eligible for
inclusion on the National Historic
Register of Historic Places (NRHP), and
to afford the Advisory Council on
Historic Preservation a reasonable
opportunity to comment on such
undertakings.
The BLM is not required to perform
ESA or NHPA consultations to rescind
the 2015 rule. Neither the rescission nor
implementation of the 2015 rule would,
by themselves, authorize or prohibit
hydraulic fracturing operations as a
whole, or any particular hydraulic
fracturing operation on Federal or
Indian lands. These actions are also not
expected to impact the number of
hydraulic fracturing operations. As
such, the actions would not, by
themselves, have an effect on any listed
species or its habitat nor any historic
properties that are listed on or eligible
for listing on the NRHP. After the 2015
rule is rescinded, the BLM will continue
to make decisions involving the
development of oil and gas resources on
BLM-administered lands at the land use
planning, leasing, and permitting stages
in compliance with NEPA, the ESA, and
the NHPA. Indeed, site-specific
proposals to drill for and develop oil
and gas resources that involve hydraulic
fracturing operations would require the
same level of compliance with the ESA
and NHPA if the BLM did not rescind
the 2015 rule. Given that the BLM
considers the cumulative and sitespecific effects of proposed oil and gas
operations as part of its land use
planning, leasing, and permitting
processes, as is discussed earlier in this
preamble, and will conduct appropriate
consultations whenever and wherever
appropriate, consultation under the ESA
and NHPA is not required at this time.
Some commenters state that, because
the issue of ‘‘frack hits’’ was not part of
the discussions between stakeholders
and the agency during the rulemaking
process for the 2015 rule, it is
reasonable that the BLM would rescind
the 2015 rule and defer issuance of any
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rule related to ‘‘frack hits’’ until the
appropriate regulatory procedures are
invoked.
Some commenters also state that the
2015 rule would have required that
before hydraulic fracturing operations
begin, the operator must perform a
successful mechanical integrity test of
any casing or fracturing string through
which the operation will be conducted.
These commenters contend that the
administrative record prepared for the
2015 final rule ‘‘does not contain
comments regarding the efficacy, cost,
or purpose of testing the lateral portion
of the wellbore because that
requirement was not part of the
proposed rule.’’
The commenters contend that
measures to protect against ‘‘frack hits’’
and requiring mechanical integrity tests
included in the 2015 rule were not
logical outgrowths of the BLM’s
proposed rule. Because the BLM is
rescinding the 2015 rule, and because
the present rule rescission does not
contain measures related to ‘‘frack hits’’
or require mechanical integrity tests, it
is unnecessary to address whether the
issues of ‘‘frack hits’’ and mechanical
integrity tests are a logical outgrowth of
the proposed rule that the BLM
published.
One commenter states that it is
impossible to reconcile a requirement to
conduct a mechanical integrity test on
casing that does not protect usable water
and it is likely to increase costs of
completing a well by $75,000 to
$100,000. Given the absence of any
benefit that will be derived from these
costs, rescission of the 2015 rule is
reasonable and appropriate.
The BLM agrees that rescission of the
2015 rule is appropriate and good
policy.
Costs of 2015 Rule and Effects on
Industry
Multiple commenters state that the
2015 rule would not be burdensome for
industry. One commenter states that
there are several problems with BLM’s
assertion that the 2015 rule ‘‘imposes
burdensome reporting requirements and
other unjustified costs on the oil and gas
industry’’ (82 FR 34464). The
commenter states first, that the BLM’s
own RIA finds that the 2015 rule would
cost approximately $9,690 per well, or
about 0.1 percent to 0.2 percent of the
cost of drilling a well (RIA at 3, Tables
4.2.2.a, 4.2.2.b). The commenter further
notes that the BLM’s estimate of the
costs of the 2015 rule have not
substantially changed since 2015 (80 FR
16,130 (estimating compliance costs to
be ‘‘approximately 0.13 to 0.21 percent
of the cost of drilling a well’’)). The
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commenter states that BLM also noted
that its cost estimates may be overstated
where industry is already in
compliance.
In the RIA for the 2015 rule, the BLM
asserted that regulation would result in
a reduction of the risks associated with
hydraulic fracturing operations on
Federal and Indian lands, without
providing an estimate for the monetary
benefits of this risk reduction. The BLM
noted in the 2015 RIA that the majority
of the requirements were consistent
with industry practice and that some
were required by state regulations or
were generally addressed by existing
BLM requirements. In light of the
protections available under other
Federal regulations, the increased
prevalence of state and tribal laws and
regulations to address hydraulic
fracturing, and new industry practices,
the BLM believes that the requirements
imposed by the 2015 rule are redundant
and therefore unnecessarily
burdensome. There were no monetary
estimates of any incremental benefit that
the 2015 rule provides in addition to
existing Federal, state, and tribal
regulations and industry standards.
Such incremental benefits, however, are
likely to be too small in light of the
increased prevalence and
comprehensiveness of these standards
since the original RIA was published to
justify compliance costs that are both
monetized and certain to exist.
One commenter notes that, in 2015, in
response to commenters’ arguments that
the rule was not economically justified
and that benefits did not exceed costs,
the BLM responded that the 2015 rule
was ‘‘prudent,’’ ‘‘necessary,’’ and
‘‘common-sense,’’ and that the rule’s
‘‘burden should be minimal.’’ The
commenter asserts that, in its proposed
rescission, the BLM never sufficiently
explains why those same prudent,
common-sense requirements, deemed
necessary to environmental protection
after weighing compliance costs, are
now suddenly unnecessary.
As noted in previous responses, in
light of the protections available under
other Federal regulations, the increased
prevalence of state and tribal laws and
regulations to address hydraulic
fracturing, and new industry practices,
the BLM now believes that the
requirements imposed by the 2015 final
rule are redundant or only marginally
beneficial, and therefore unnecessarily
burdensome.
One commenter states that the BLM
fails to acknowledge the forgone cost
savings of the tank requirement that will
partly offset any estimated cost savings
from the rescission. The commenter
notes that storage tank requirement from
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the 2015 rule was anticipated to
generate long-term cost savings for
industry that would have partly offset
their compliance costs. The commenter
suggests that rescinding the requirement
will forgo those cost savings, and that
loss of cost savings will partly offset any
positive cost savings anticipated from
the rescission.
In response to the previous comment,
the BLM notes that it is not clear that
requiring operators to use storage tanks
for flowback and produced water would
generate any cost savings. Operators that
instead use central reservoirs may have
decided to do so precisely because it is
the most cost-effective option available
to them, and requiring them to do
otherwise may have the unintended
consequence of increasing costs for
them.
One commenter states that an
unanticipated cost associated with
rescinding the 2015 rule is related to
road and infrastructure damage
associated with trucks hauling large
quantities of salt water and drilling mud
at load weights exceeding legal limits by
35 percent. The commenter offers that
Texas has incurred more than $2 billion
debt to repair about 40 percent of their
damaged roads in absence of having a
dedicated revenue source to pay for it.
A commenter states that failure to hold
businesses accountable for their
externalities amounts to indirect
subsidies, which is not fair to producers
of clean energy who do not receive these
advantages. The commenter states that
Federal lands are leased to these
extractors at prices that are well below
market values for extraction on private
lands. The commenter asserts that this
is another indirect subsidy for the
extractors and is a bad deal for the
taxpayers.
The use of public roads for the
transport of materials and equipment
both to and from energy production
sites, including weight restrictions and
taxation, is regulated by states and
localities, and on tribal lands by tribes.
It was not addressed in the 2015 rule,
and thus is outside the scope of this
rulemaking. Operators do need BLM’s
approval for access roads from public
roads across public lands to their
operation sites.
The BLM also disagrees with the
assertion that Federal lands are leased at
‘‘well below market values’’ for oil and
gas extraction on comparable private
lands. Although private leases may
often have higher royalty rates, there are
often greater regulatory burdens
uniquely associated with Federal
leasing requirements. These include
NEPA reviews for leasing nominations
and drilling permits, production
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measurement compliance requirements,
and other fees and assessments, that
operators do not encounter to the same
extent on non-Federal lands. A simple
comparison of royalty rates between
Federal and non-Federal oil and gas
leases is insufficient to support the
commenter’s conclusion about market
values. Furthermore, bonus bids, rentals
and royalties are outside the scope of
this rulemaking.
One commenter suggests that
California’s growing economy is an
example to counter industry’s claims
that the 2015 rule and regulations in
general, unnecessarily encumber energy
production, constrain economic growth,
and prevent job creation.
The commenter does not provide
evidence that regulation of hydraulic
fracturing in California specifically has
an impact on statewide economic
growth. Also, different states have
different mixes of industries and
employers, as well as different geology,
land ownership patterns, and other
conditions important to business
growth. Thus, we have no reasonable
basis to extrapolate from any state’s
economic growth to a conclusion that
the 2015 rule would be a net benefit for
job creation.
One commenter suggested it is
valuable to have a unified standard with
which to regulate hydraulic fracturing.
The commenter states that frack hits
also pose a threat to industry profits, as
they may also lead to a decrease in well
production. The commenter states that,
without firmly regulating irresponsible
drilling practices, we run the risk of not
only damaging the ecological health of
our public lands and water resources,
but also sabotaging the success of the
extractive industry.
As noted in the RIA, the American
Petroleum Institute does provide
uniform, national voluntary standards
for conducting hydraulic fracturing.
Hydraulic fracturing oversight is and
will continue to be provided through
the state laws and regulations detailed
in API 100–1 and API 100–2. There is
ample evidence from national
production data that hydraulic
fracturing allows oil and gas production
that would not otherwise be realized.
Any frack hits on neighboring wells
from using the technology are
unfortunate but not nationally
significant compared to the overall
industry growth emanating from this
technology.
One commenter suggests that, because
the 2015 rule presented significant
conflicts with existing Federal and state
regulations, its adoption held the
potential to create regulatory
uncertainty and confusion, increasing
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project costs, thus providing further
disincentives to operators to develop
resources on Federal lands that the
agency manages for the American
people.
The BLM does not agree that
regulations that are largely consistent
with state rules and industry practices
necessarily increase uncertainty or
confusion. The BLM does agree,
however, that such overlap can make
such regulations redundant, marginally
beneficial, and unnecessarily
burdensome, which is the why it is
rescinding the 2015 rule.
Multiple commenters state that
additional BLM regulation of a process
already regulated by the states will
decrease efficiency and increase costs.
Commenters assert that the BLM does
not have the staff, the budget, or the
expertise to process APDs with the same
efficiency as the states. One commenter
states that the delay in processing APDs
by the BLM will result in declining
production from Federal lands to the
detriment of the public. Another
commenter asserts that the BLM
severely underestimated the cost of the
2015 rule by not including the cost of
delays in permit approval. The
commenter asserts that if APDs are not
approved in a timely manner, the releasing process will cost additional
millions. A separate commenter
highlights that BLM officials conceded
that, given the combination of increases
in workload associated with the
hydraulic fracturing rule and reductions
in the agency budget, getting the work
done could be an issue. The commenter
also notes that, among other problems,
the BLM recognizes that ‘‘skills gaps’’
are a ‘‘program vulnerability’’ for the
BLM’s existing oil and gas programs.
The commenter therefore concludes that
rescission of the 2015 rule is entirely
appropriate given the admonitions of
agency leaders that the BLM does not
have the expertise in the field to
administer the rule.
The BLM’s engineers and field
managers have decades of experience
exercising oversight of these wells
during the evolution of hydraulic
fracturing technology. However, as
stated in the RIA for this rule, the BLM
recognizes the potential that the 2015
rule might pose unnecessary delays and
implementation costs to the BLM and
operators. These costs were not
quantified in the RIA for the 2015 rule.
The BLM’s staffing levels, budget and
appropriations are outside the scope of
this rulemaking.
One commenter argues that, due to
North Dakota’s unique history of land
ownership, it is typical for oil and gas
spacing units to consist of a
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combination of Federal, state, and
private mineral ownership. The
commenter notes that, even in
circumstances where the Federal
mineral ownership within a spacing
unit is small relative to other mineral
ownership, the 2015 rule would have
required all the oil and gas operators
within the unit, as a practical matter, to
conduct operations in accordance with
the 2015 rule applicable to the
development of Federal minerals. The
commenter asserts that complying with
the Federal requirements and permitting
timelines imposed by the 2015 final rule
will substantially delay operations on
any spacing units that contain Federal
minerals and that this delay adversely
affects the development of all minerals
within the unit, including state and
private oil and gas minerals.
As stated in the RIA for this rule, the
BLM recognizes the potential that the
2015 final rule might pose unnecessary
delays and implementation costs to the
BLM and operators. We understand the
commenter’s concerns that many long
directional wells are completed in many
tracts, some Federal, and some not
federal. The operators’ burdens of
complying with the 2015 rule could
adversely affect the owners of the nonfederal tracts. Those concerns support
the BLM’s decision to rescind the 2015
rule.
Some commenters state that the 2015
rule would have represented an
expansion of the information that oil
and gas developers are required to
disclose publicly both before and after
operations and that, much of this
information, and particularly
information regarding local geology and
the operators’ technical designs for
extracting resources from that geology,
is highly proprietary and represents
economically valuable commercial
information. The commenters argue that
the 2015 rule failed to account both for
the confidential nature of the
information the rule required to be
disclosed and the commercial
consequences of that disclosure. The
commenters state that, because the 2015
rule would have required public
disclosure of highly confidential and
commercially valuable information, it is
contrary to Federal public records law
and its rescission is appropriate.
Another commenter argued that the
same requirement of the 2015 rule failed
to account for service companies
owning the trade secrets.
As the commenter notes, by
rescinding the 2015 rule, the BLM
would no longer require that the
operator submit information to the BLM
and/or FracFocus after the hydraulic
fracturing operation is complete. As
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stated in the RIA, the removal of this
requirement would alleviate some
administrative burden. At least for
Federal wells, operators are likely to
report the chemicals used regardless of
whether the BLM requires them to or
not, since almost all states currently
have chemical disclosure requirements.
One commenter estimates that the
2015 rule would have imposed a
minimum per-well additional cost of
$1,500 associated with assembling,
analyzing and adding new information
to APDs and final reports submitted to
the BLM, not including the potential
additional costs associated with legal
review and requirements for the
operator to verify and manage
proprietary information that is claimed
to be exempt from disclosure. The
commenter estimates the following
additional costs of the 2015 rule:
Potential work stoppage during
completions if there is a ‘‘false positive’’
500 psi increase in annulus pressure
(assumed $200,000 to $500,000 per day
standby cost); managing ‘‘recovered
fluids’’ or produced water by
constructing and utilizing a central
storage and treatment facility according
to rule requirements (estimated 5-year
net present cost of $2.3 million for a
lined pit, vs. $23 million for using 500barrel tanks to provide a storage
capacity of 250,000 barrels); concern
that a BLM field office could interpret
the 2015 rule in a more stringent fashion
than intended, which could lead to a
slowdown, stoppage, or delay of work,
or additional costs for specific
requirements.
The BLM acknowledges that there are
several potential compliance costs for
the 2015 rule that it did not quantify in
the economic analysis that was prepared
for that rule. However, because this final
rule rescinds the 2015 rule, it is not
necessary to review whether the BLM’s
cost estimates for that rule were
adequate, or to determine if the
commenters’ estimates are appropriate.
A commenter critiqued the effects of
the 2015 rule on operators, concluding
that the rule would have caused
unintended burdens or delays.
Because we are rescinding the 2015
rule, there is no need to analyze the
commenters’ predictions.
One commenter asserts that small
businesses will benefit from this final
rule because elimination of the 2015
rule would eliminate any future
possibility that they must pay the
compliance costs associated with the
rule.
We agree that small businesses would
benefit to the degree that they are no
longer subject to the compliance costs
associated with the 2015 rule.
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One commenter states that a
comprehensive analysis of the costs the
2015 rule would have imposed
demonstrates that costs savings
resulting from the rule’s rescission are
likely to exceed $220 million per year
due to increased administrative costs
($17.8M), delay costs ($6.7M),
additional casing costs ($174M),
additional mechanical integrity testing
costs ($17M), and additional costs of
recovered fuel storage ($4.9M).
The comment has been considered in
developing the final regulatory impact
analysis (RIA), but we find that the
estimated cost savings discussed in the
RIA are more supportable and are
adequate for the decision to rescind the
2015 rule.
Regional and National Implications
One commenter states that the
economic impact of rescinding the 2015
final rule on the outdoor industry and
farming should be seriously considered
when evaluating whether rescinding the
2015 rule is good for economic growth
and job creation. The commenter asserts
that hydraulic fracturing operations
effectively destroy natural and rural
areas integral to the outdoor industry.
The commenter notes that, in 2011, the
outdoor industry employed 6.1 million
Americans and Americans spend
approximately $646 billion annually on
outdoor recreation.
There is little to no evidence that
properly regulated hydraulic fracturing
operations have a significantly greater
effect on natural and rural areas integral
to the outdoor industry compared to the
conventional oil and gas drilling
operations that have taken place on
BLM lands for decades. In its decision
to rescind the 2015 rule, the BLM
examined existing state regulations—as
well as existing Federal regulations
contained in Onshore Orders 1, 2, and
7—and determined that they are
sufficient to ensure that hydraulic
fracturing operations on Federal lands
remain properly regulated.
To the degree that lands open for oil
and gas development could have an
opportunity cost in that they could
otherwise be used for recreational
activities, the BLM has long
implemented FLPMA’s policy of
multiple use that uses the NEPA
environmental review process to
determine how best to plan for the
public’s desires to put the lands to
competing uses. The BLM’s land use
planning, however, is beyond the scope
of this rulemaking.
Multiple commenters support the
proposed rescission asserting that the
2015 rule imposes unnecessary costs,
hinders energy production, and
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constrains economic growth.
Commenters argue that the potential
cost impacts of the 2015 rule on
exploration and production activities on
BLM managed lands would greatly
exceed the estimates that the BLM
provided in its original RIA. One
commenter asserts that governments
should take care to ensure that any
regulations they issue to ensure safety
and protect the environment recognize
the economic importance of, and avoid
unduly burdening the use of, hydraulic
fracturing to develop America’s energy
resources.
In analyzing the 2015 rule, the BLM
has reached the same conclusion
regarding its unnecessary costs and
impact on energy production and
economic growth. As a result, the BLM
has decided to rescind the 2015 rule.
One commenter stated that BLM’s
2015 rule would exacerbate the decline
in oil and natural gas production on
Federal lands and that this would have
a severe, negative effect on Wyoming’s
tax revenue and employment numbers,
would increase the costs for energy to
all consumers, and could increase this
country’s reliance on imports from less
than friendly nations.
Regardless of whether the 2015 rule
would have had a ‘‘severe, negative
effect’’ on any state, or whether it would
have caused an increase in reliance
upon imported oil or gas, the BLM does
believe that the costs of complying with
the 2015 rule would be an unnecessary
burden on industry. This
Administration’s policy is to increase
revenues and to reduce reliance on
imported oil through this and other
actions to reduce unnecessary burdens
on energy industries, including oil and
gas on Federal and Indian lands. Thus,
we are rescinding the 2015 rule.
Climate Change
Some commenters contend that the
BLM cannot, in evaluating its oversight
of hydraulic fracturing on the public
lands, overlook the fact that extracting
the new oil and gas resources made
exploitable by modern hydraulic
fracturing techniques is inconsistent
with any reasonable likelihood of
avoiding the most catastrophic effects of
global climate change. Some
commenters recommend that the United
States shift toward alternative forms of
energy.
Some commenters assert that the BLM
must weigh the relative effects on oil
and gas production, supply, markets,
and ultimately emissions of its actions
in regulating public lands hydraulic
fracturing. The commenters assert that
this must include an assessment of the
net emissions consequences of all
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reasonable alternatives—including
implementation of the 2015 hydraulic
fracturing rule, the BLM’s proposed
rescission of that rule, or an alternative
rule banning public lands hydraulic
fracturing.
Those commenters seek a reduction in
leasing and production of oil and gas
from Federal and Indian lands with the
goal of reducing emissions of
greenhouse gasses. Issues of land use
planning, leasing of parcels, and levels
of production from Federal and Indian
lands are beyond the scope of this
rulemaking. Hydraulic fracturing was a
technology available to operators on
Federal and Indian lands prior to the
promulgation of the 2015 rule, it would
have been available had the 2015 rule
become effective, and it will be
available after promulgation of this
rescission rule. The BLM is committed
to compliance with NEPA at each stage
of its decision-making. NEPA does not
require the BLM to consider banning
hydraulic fracturing in its analysis of
this rescission rule. As previously
stated, the purpose and need for the rule
is to reduce unnecessary burdens on oil
and gas production from Federal and
Indian lands. Furthermore, since
emission levels from future hydraulic
fracturing operations are necessarily
speculative (because they depend upon
geologic, technical, and economic
variables, plus the potential substitution
of sources for oil and gas), a comparison
of ‘‘net emissions consequences’’ would
not provide useful information to the
decision-maker or the public.
The BLM has not made a change from
the 2017 proposed rule to this final rule
in response to those comments.
Recommendations
Multiple commenters suggest the
BLM should conduct additional
research regarding the impacts of
hydraulic fracturing and of rescinding
the 2015 rule, including the impacts of
hydraulic fracturing on drinking water
resources and human health. Some
commenters assert that the BLM must
thoroughly study the effects of repealing
the rule, including consideration of new
circumstances, studies, and information
developed since the rule was adopted.
The commenters assert that this should
include, for example, consideration of
recent information regarding
connections between disposal of
drilling-related waste and earthquakes,
according to some commenters.
Moreover, the commenters state that the
BLM must consider the likelihood that
the proposed deregulation will lead to a
significant expansion in poorly
controlled oil and gas drilling and
hydraulic fracturing and the
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consequences for global climate change.
Some commenters suggest that the BLM
should consider and adopt a rule that
protects public lands, public health, and
the climate by banning hydraulic
fracturing altogether on public lands.
In response to the previous
comments, the BLM notes that, in
December 2016, EPA completed its
nationwide study of hydraulic
fracturing. U.S. EPA, Hydraulic
Fracturing for Oil and Gas: Impacts from
the Hydraulic Fracturing Water Cycle on
Drinking Water Resources in the United
States (Final Report), EPA/600/R–16/
236F (available at 2016https://
cfpub.epa.gov/ncea/hfstudy/
recordisplay.cfm?deid=332990). The
BLM has considered the findings in that
report. That report demonstrated that,
like most industrial processes, hydraulic
fracturing has the potential to cause the
release of pollutants into the
environment, including groundwater
resources. A logical conclusion is that
hydraulic fracturing activities should be
regulated to control those risks. It is not
clear, however, that the 2015 rule was
the best or only way to regulate
hydraulic fracturing on Federal and
Indian lands. Commenters have failed to
provide facts demonstrating that the
BLM needs to conduct another study a
year after EPA’s report. Risks of induced
seismicity from hydraulic fracturing
operations are beyond the scope of this
rulemaking. The USGS studies both
natural and induced seismicity. Several
USGS publications are listed at https://
earthquake.usgs.gov/research/induced/
references.php. Those studies show that
induced seismicity from hydraulic
fracturing operations is uncommon, and
seems to occur mostly in areas with
small percentages of federally owned
minerals. More common is seismicity
induced by the injection of waste fluids
for disposal. Those disposal wells,
however, are regulated by states, tribes
and the EPA under the Safe Drinking
Water Act, and are beyond the scope of
this rulemaking.
This final rule will not lead to poorly
regulated drilling of oil and gas wells on
Federal and Indian lands. Drilling
operations will continue to be subject to
the BLM’s regulations, including
Onshore Oil and Gas Order No. 2, (53
FR 46798, 1988), state regulations on
Federal land, and tribal regulations on
tribal lands. We do not believe that
hydraulic fracturing operations will be
poorly regulated under the present rule,
with states and tribes taking the lead for
regulating most hydraulic fracturing
activities.
As previously explained, we do not
believe it is in the national interest to
ban hydraulic fracturing on Federal and
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61945
Indian lands. Hydraulic fracturing
activities can be conducted in ways that
reduce risks to the environment while
providing the benefits of domestically
produced oil and gas, including jobs.
Furthermore, a ban on hydraulic
fracturing on Federal and Indian lands
would most likely cause production to
move to areas that are not subject to the
BLM’s regulations, and have no impact
on emissions.
One commenter asserts that the 2015
rule provides for a ‘‘type well’’ to be
used for an entire field to satisfy the prefracturing approval requirements. The
commenter recommends that the 2015
rule should be rescinded in its entirety
or expanded to allow a type well to
cover an entire county or basin if the
geology is substantially similar.
The commenter is mistaken. The 2015
rule does not mention a ‘‘type well.’’
The present rule rescinds the 2015 rule
in its entirety.
The BLM has not made a change from
the 2017 proposed rule to this final rule
based on these commenters’
recommendations.
Discussion of the Final Rule
As previously discussed in this
preamble, the BLM is revising 43 CFR
part 3160 to rescind the 2015 rule. The
regulatory amendments in this final rule
are identical to those in the proposed
rule, except that the phrase ‘‘perform
nonroutine fracturing jobs’’ has been
removed from the regulations at 43 CFR
3162.3–2(a). This final rule restores the
regulations in part 3160 of the CFR to
exactly as they were before the 2015
rule, except for changes to those
regulations that were made by other
rules published between March 26, 2015
(the date of publication of the 2015 final
rule) and now, and the phrase ‘‘perform
nonroutine fracturing jobs,’’ which is
not restored to the list of subsequent
operations requiring prior approval in
section 3162.3–2(a). None of the
amendments to part 3160 by other rules
are relevant to this rulemaking. See, e.g.,
82 FR 83008 (2016). The following
section-by-section analysis discusses
returning to the pre-2015 rule
regulations.
Section 3160.0–3
Authority
The BLM amends § 3160.0–3 by
removing the reference to the Federal
Land Policy and Management Act of
1976, as amended (43 U.S.C. 1701). The
2015 rule added this reference as an
administrative matter. This final rule
returns this section to the language it
contained before the 2015 rule and does
not have any substantive impact.
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Section 3160.0–5
Definitions
The BLM amends this section by
removing several terms that were added
by the 2015 rule and by restoring the
definition of ‘‘fresh water’’ that the 2015
rule removed. This final rule removes
the definitions of ‘‘annulus,’’
‘‘bradenhead,’’ ‘‘Cement Evaluation Log
(CEL),’’ ‘‘confining zone,’’ ‘‘hydraulic
fracturing,’’ ‘‘hydraulic fracturing
fluid,’’ ‘‘isolating or to isolate,’’ ‘‘master
hydraulic fracturing plan,’’ ‘‘proppant,’’
and ‘‘usable water.’’ The 2015 rule used
those terms in the operating regulations.
Since those operating regulations are
rescinded, these terms are no longer
necessary in this definitions section.
This final rule restores the previous
definition of ‘‘fresh water’’ to the
regulations.
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Section 3162.3–2
Operations
Subsequent Well
This final rule amends § 3162.3–2 by
making non-substantive changes to
paragraph (a), which include replacing
the word ‘‘must’’ with the word ‘‘shall,’’
replacing the word ‘‘combine’’ with the
word ‘‘commingling,’’ replacing the
word ‘‘convert’’ with the word
‘‘conversion,’’ and removing the
language from the first sentence of
paragraph (a) that the 2015 rule only
added to more fully describe Form
3160–5.
In response to comments received,
§ 3162.3–2(a) of this final rule does not
include the requirement to obtain prior
approval to ‘‘perform nonroutine
fracturing jobs.’’ As previously
discussed in this preamble, as a result
of considerable advances in oil and gas
development technology in the last 20
years, hydraulic fracturing practices that
would have been considered
‘‘nonroutine’’ when the BLM originally
issued the regulations requiring prior
approval for ‘‘nonroutine fracturing
jobs’’ are now commonly employed and
considered ‘‘routine.’’ See the ‘‘Rule
Authorities’’ discussion of comments for
more information about this revision.
The final rule makes non-substantive
changes to paragraph (b) of § 3162.3–2,
which include replacing ‘‘using a
Sundry Notice and Report on Well
(Form 3160–5)’’ with ‘‘on Form 3160–
5.’’
The final rule restores ‘‘routine
fracturing or’’ to paragraph (b) of
§ 3162.3–2. The 2015 rule removed
those words from the list because it
amended § 3162.3–3 to include a
detailed listing of requirements for
hydraulic fracturing operations to be
approved by the authorized officer. This
final rule removes that requirement
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from § 3163.3–3, which is discussed
below.
Section 3162.3–3 Other Lease
Operations
The BLM revises this section by
removing language that was added by
the 2015 rule and returning this rule to
the exact language it contained
previously. The 2015 rule made
substantial changes to this section and
revised the title to read as ‘‘Subsequent
well operations; Hydraulic fracturing.’’
Paragraph (a) of this section in the
2015 rule, as reflected in the 2015
edition of the CFR, includes an
implementation schedule that the BLM
would have followed to phase in the
requirements of the rule, had the rule
gone into effect. Paragraph (b) of this
section contains the performance
standard referencing § 3162.5–2(d).
Paragraph (c) of this section would have
required prior approval of hydraulic
fracturing operations. Paragraph (d) of
this section lists the information that an
operator would have been required to
include in a request for approval of
hydraulic fracturing. Paragraph (e) of
this section specifies how an operator
would have had to monitor and verify
cementing operations prior to hydraulic
fracturing. Paragraph (f) of this section
would have required mechanical
integrity testing of the wellbore prior to
hydraulic fracturing. Paragraph (g) of
this section would have required
monitoring and recording of annulus
pressure during hydraulic fracturing.
Paragraph (h) of this section specifies
the requirements that would have
applied for managing recovered fluids
until approval of a permanent water
disposal plan. Paragraph (i) of this
section specifies information that an
operator would have been required to
provide to the authorized officer after
completion of hydraulic fracturing
operations. Paragraph (j) of this section
specifies how an operator could have
withheld information from the BLM and
the public about the chemicals used in
a hydraulic fracturing operation.
Paragraph (k) of this section describes
how the BLM would have approved
variances from the requirements of the
2015 final rule.
For the reasons discussed earlier in
this preamble, the BLM believes this
section of the 2015 rule is unnecessarily
duplicative and would impose costs that
would not be clearly exceeded by its
benefits and, therefore, removes these
2015 rule provisions and restores the
previous language of the section.
Section 3162.5–2 Control of Wells
The BLM amends paragraph (d) of
this section by restoring the term ‘‘fresh
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water-bearing’’ and the phrase
‘‘containing 5,000 ppm or less of
dissolved solids.’’ The final rule also
restores other non-substantive
provisions that appeared in the previous
version of the regulations.
Good Cause for Immediate Effectiveness
The APA normally requires
regulations to become effective no
sooner than 30 days after publication in
the Federal Register (5 U.S.C. 553(d)).
Nonetheless, the APA allows
regulations to go into effect immediately
upon publication when ‘‘a substantive
rule grants or recognizes an exemption
or relieves a restriction’’ (5 U.S.C.
553(d)(1)). As explained in this
preamble, this final rule relieves oil and
gas operators on Federal and Indian
lands from the numerous restrictions
and burdens that would be imposed if
the 2015 rule were to go into effect.
The primary purpose of the delayed
effective date requirement in section
553(d) is to give people a reasonable
time to prepare to comply with or take
other action with respect to the rule (See
Attorney General’s Manual on the
Administrative Procedure Act 37
(1947)). As explained elsewhere in this
preamble, the 2015 rule has never been
operational. Therefore, no one requires
time to conform their conduct to avoid
the legal consequences of ‘‘violating’’
the regulations that would remain in
effect after rescission of the 2015 rule.
Even if persons not subject to the 2015
rule could claim a benefit from a 30-day
effective date, that would not prevent
this final rule from becoming effective
immediately upon publication
(Independent U.S. Tanker Owners
Comm. v. Skinner, 884 F.2d 587, 591–
92 (D.C. Cir. 1989), cert. denied, 495
U.S. 904 (1990)).
The APA also allows regulations to go
into effect immediately upon
publication for ‘‘good cause’’ (5 U.S.C.
553(d)(3)). Application of the good
cause exception requires an ‘‘ ‘urgency
of conditions coupled with
demonstrated and unavoidable
limitations of time,’ ’’ with the ‘‘primary
consideration . . . be[ing] the
‘convenience or necessity of the people
affected’ ’’ (United States v. Gavrilovic,
551 F.2d 1099, 1104 (8th Cir. 1977)
(quoting 92 Cong. Rec. 5650–51 (1946)
(remarks of Cong. Walter))). In
determining whether to invoke the good
cause exception, an ‘‘agency is required
to balance the [public] necessity for
immediate implementation against
principles of fundamental fairness
which require that all affected persons
be afforded a reasonable time to prepare
for the effective date of its ruling’’
(Gavrilovic, 551 F.2d at 1105).
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The current posture of the litigation
related to the 2015 rule makes it
possible that the 2015 rule could
become operational within 30 days of
the publication of this final rule. Were
that to happen, oil and gas operators—
the persons most affected by this final
rule—would have to go to significant
expense to comply with the 2015 rule,
even though that rule would be
rescinded in a matter of days upon the
effective date of this final rule. Those
significant burdens would not be offset
by the de minimus environmental
benefits of a few days of compliance
with the 2015 rule. Requiring oil and
gas operators to incur such significant
expense to comply with a rule that will
be rescinded in a matter of days would
be fundamentally unfair. Thus, there are
urgent conditions, unavoidable
limitations of time, and a risk to the
convenience or necessity of the people
affected.
For both of these reasons, the BLM
finds that there is good cause for this
final rule to be effective upon
publication in the Federal Register.
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III. Procedural Matters
Regulatory Planning and Review
(Executive Orders 12866, 13563, and
13771)
Executive Order 12866 provides that
the Office of Information and Regulatory
Affairs in the Office of Management and
Budget will review all significant rules.
The Office of Information and
Regulatory Affairs has determined that
this rule is significant because it will
raise novel legal or policy issues.
Executive Order 13563 reaffirms the
principles of Executive Order 12866
while calling for improvements in the
Nation’s regulatory system to promote
predictability, to reduce uncertainty,
and to use the best, most innovative,
and least burdensome tools for
achieving regulatory ends. The
Executive Order directs agencies to
consider regulatory approaches that
reduce burdens and maintain flexibility
and freedom of choice for the public
where these approaches are relevant,
feasible, and consistent with regulatory
objectives. E.O. 13563 emphasizes
further that regulations must be based
on the best available science and that
the rulemaking process must allow for
public participation and an open
exchange of ideas. We have developed
this rule in a manner consistent with
these requirements.
Executive Order 13771 (82 FR 9339,
Feb. 3, 2017) requires Federal agencies
to take proactive measures to reduce the
costs associated with complying with
Federal regulations. Consistent with
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Executive Order 13771, we have
estimated the cost savings for this final
rule to be $14—$34 million per year
from the 2015 rule. Therefore, this final
rule is expected to be a deregulatory
action under Executive Order 13771.
Regulatory Flexibility Act
The BLM certifies that this rule will
not have a significant economic effect
on a substantial number of small entities
pursuant to 5 U.S.C. 605(b). The
Regulatory Flexibility Act (5 U.S.C. 601
et seq.) (RFA) generally requires that
Federal agencies prepare a regulatory
flexibility analysis for rules subject to
the notice and comment rulemaking
requirements under the Administrative
Procedure Act (5 U.S.C. 500 et seq.), if
the rule would have a significant
economic impact, either detrimental or
beneficial, on a substantial number of
small entities (See 5 U.S.C. 601—612).
Congress enacted the RFA to ensure that
government regulations do not
unnecessarily or disproportionately
burden small entities. Small entities
include small businesses, small
governmental jurisdictions, and small
not-for-profit enterprises.
The BLM reviewed the Small
Business Administration (SBA) size
standards for small businesses and the
number of entities fitting those size
standards as reported by the U.S.
Census Bureau in the Economic Census.
The BLM concluded that the vast
majority of entities operating in the
relevant sectors are small businesses as
defined by the SBA. As such, the final
rule will likely affect a substantial
number of small entities.
Although the final rule will likely
affect a substantial number of small
entities, the BLM does not believe that
these effects would be economically
significant. This final rule is a
deregulatory action that will remove all
of the requirements placed on operators
by the 2015 rule. Operators will not
have to undertake the compliance
activities, either operational or
administrative, that are outlined in the
2015 rule, except to the extent the
activities are required by state or tribal
law, or by other pre-existing BLM
regulations.
The BLM conducted an economic
analysis which estimates that the
average reduction in compliance costs
will be a small fraction of a percent of
the profit margin for small companies,
which is not a large enough impact to
be considered significant. For more
detailed information, see section 5.3 of
the RIA prepared for this final rule. The
final RIA has been posted in the docket
for the final rule on the Federal
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eRulemaking Portal: https://
www.regulations.gov.
Small Business Regulatory Enforcement
Fairness Act (SBREFA)
This rule is not a major rule under 5
U.S.C. 804(2), the Small Business
Regulatory Enforcement Fairness Act.
This rule will not cause a major increase
in costs or prices for consumers,
individual industries, Federal, state, or
local government agencies, or
geographic regions. The rule will not
have an annual effect on the economy
of $100 million or more.
This rule will not cause a major
increase in costs or prices for
consumers, individual industries,
Federal, state, or local government
agencies, or geographic regions.
This rule will not have significant
adverse effects on competition,
employment, investment, productivity,
innovation, or the ability of U.S.-based
enterprises to compete with foreignbased enterprises.
This final rule is a deregulatory action
that removes all of the requirements
placed on operators by the 2015 rule.
Operators will not have to undertake the
compliance activities, either operational
or administrative, that would have been
required solely by the 2015 rule. The
screening analysis conducted by the
BLM estimates the average reduction in
compliance costs will be a small
fraction of a percent of the profit margin
for companies, which is not large
enough to: Have significant adverse
effects on competition, employment,
investment, productivity, innovation, or
the ability of U.S.-based enterprises to
compete with foreign-based enterprises;
cause a major increase in costs or prices
for consumers, individual industries,
Federal, state, or local government
agencies, or geographic regions; or have
an annual effect on the economy of $100
million or more.
Unfunded Mandates Reform Act
This rule does not impose an
unfunded mandate on state, local, or
tribal governments, or the private sector
of more than $100 million per year. The
rule does not have a significant or
unique effect on State, local, or tribal
governments or the private sector. A
statement containing the information
required by the Unfunded Mandates
Reform Act (2 U.S.C. 1531 et seq.)
(UMRA) is not required. This rule is
also not subject to the requirements of
section 203 of UMRA because it
contains no regulatory requirements that
might significantly or uniquely affect
small governments, because it contains
no requirements that apply to such
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in clear language with clear legal
standards.
Takings (EO 12630)
This rule does not affect a taking of
private property or otherwise have
taking implications under Executive
Order 12630. A takings implication
assessment is not required. This rule is
a deregulatory action that removes all of
the requirements placed on operators
solely by the 2015 rule and therefore
will impact some operational and
administrative requirements on Federal
and Indian lands. All such operations
are subject to lease terms which
expressly require that subsequent lease
activities be conducted in compliance
with subsequently adopted Federal laws
and regulations. This rule conforms to
the terms of those leases and applicable
statutes and, as such, the rule is not a
government action capable of interfering
with constitutionally protected property
rights. Therefore, the BLM has
determined that the final rule will not
cause a taking of private property or
require further discussion of takings
implications under Executive Order
12630.
Consultation With Indian tribes (E.O.
13175 and Departmental Policy)
Federalism (E.O. 13132)
Under the criteria in section 1 of
Executive Order 13132, this rule does
not have sufficient federalism
implications to warrant the preparation
of a federalism summary impact
statement. A federalism summary
impact statement is not required. The
final rule will not have a substantial
direct effect on the states, on the
relationship between the Federal
Government and the states, or on the
distribution of power and
responsibilities among the levels of
government. It will not apply to states
or local governments or state or local
governmental entities. The rule will
affect the relationship between
operators, lessees, and the BLM, but it
does not directly impact the states.
Therefore, in accordance with Executive
Order 13132, the BLM has determined
that this final rule does not have
sufficient federalism implications to
warrant preparation of a federalism
assessment.
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governments, nor does it impose
obligations upon them.
Civil Justice Reform (E.O. 12988)
This rule complies with the
requirements of Executive Order 12988.
More specifically, this rule meets the
criteria of section 3(a), which requires
agencies to review all regulations to
eliminate errors and ambiguity and to
write all regulations to minimize
litigation. This rule also meets the
criteria of section 3(b)(2), which
requires agencies to write all regulations
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National Environmental Policy Act
The Department strives to strengthen
its government-to-government
relationship with Indian tribes through
a commitment to consultation with
Indian tribes and recognition of their
right to self-governance and tribal
sovereignty. The BLM has evaluated this
final rule in accordance with the
Department’s consultation policies and
under the criteria in Executive Order
13175. The BLM authorizes oil and gas
operations that are proposed on Indian
onshore oil and gas leases. Therefore,
the rule has the potential to affect
Indian tribes and tribal lands.
Potentially affected tribes were
provided an opportunity to provide
feedback and consult with the BLM
regarding this rule. The BLM has fully
considered tribal views made known to
us in preparing this final rule.
The BLM prepared an environmental
assessment (EA) to document its
examination of the potential
environmental impacts that may occur
as a result of this final rule. The BLM
has determined that this rule does not
constitute a major Federal action
significantly affecting the quality of the
human environment. A detailed
statement under the National
Environmental Policy Act of 1969 is not
required because we reached a Finding
of No Significant Impact (FONSI) for
this final rule.
The final EA and FONSI that were
prepared for this final rule have been
placed in the file for the BLM’s
Administrative Record for the final rule
at the BLM’s 20 M Street address
specified in the ADDRESSES section. The
final EA and FONSI have also been
posted in the docket for the final rule on
the Federal eRulemaking Portal: https://
www.regulations.gov. The BLM invites
the public to review these documents.
Paperwork Reduction Act (44 U.S.C.
3501 et seq.)
Effects on the Energy Supply (E.O.
13211)
The Paperwork Reduction Act (PRA)
(44 U.S.C. 3501–3521) provides that 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 control
number issued by the Office of
Management and Budget (OMB).
Collections of information include
requests and requirements that an
individual, partnership, or corporation
obtain information, and report it to a
Federal agency. See 44 U.S.C. 3502(3);
5 CFR 1320.3(c) and (k).
This rule rescinds information
collection activities that would have
required approval by the OMB under
the PRA had the 2015 rule become
effective. OMB pre-approved those
activities and assigned control number
1004–0203 to them, but the control
number was not activated. In view of
the rescission, there will be no need to
continue the information collection
activities that the OMB has preapproved under control number 1004–
0203. Accordingly, the BLM will request
that the OMB discontinue that control
number after the effective date of this
final rule.
In accordance with this final rule, the
BLM will include in its request for
renewal of control number 1004–0137
(expires January 31, 2018) that
nonroutine fracturing jobs be removed
from the information collection activity
for subsequent well operations, at 43
CFR 3162.3–2.
This final rule is not a significant
energy action under the definition in
Executive Order 13211. A statement of
Energy Effects is not required. Section
4(b) of Executive Order 13211 defines a
‘‘significant energy action’’ as ‘‘any
action by an agency (normally
published in the Federal Register) that
promulgates or is expected to lead to the
promulgation of a final rule or
regulation, including notices of inquiry,
advance notices of rulemaking, and
notices of rulemaking: (1)(i) That is a
significant regulatory action under
Executive Order 12866 or any successor
order, and (ii) is likely to have a
significant adverse effect on the supply,
distribution, or use of energy; or (2) that
is designated by the Administrator of
[OIRA] as a significant energy action.’’
Since this final rule is a deregulatory
action and would reduce compliance
costs, it is likely to have a positive
effect, if any, on the supply,
distribution, or use of energy, and not a
significant adverse effect. As such, we
do not consider the final rule to be a
‘‘significant energy action’’ as defined in
Executive Order 13211.
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Fmt 4701
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Authors
The principal author(s) of this rule are
Justin Abernathy, Senior Policy Analyst,
BLM, Washington Office; Michael Ford,
Economist, BLM, Washington Office;
James Tichenor, Economist, BLM,
Washington Office; Ross Klein, (Acting)
Natural Resource Specialist, BLM,
Washington Office; Subijoy Dutta, Lead
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Petroleum Engineer, BLM, Washington
Office; Jeffrey Prude, Petroleum
Engineer/Oil and Gas Program Lead,
BLM, Bakersfield Field Office; and
James Annable, Petroleum Engineer,
BLM, Royal Gorge Field Office; assisted
by Charles Yudson of the BLM’s
Division of Regulatory Affairs and by
Richard McNeer and Ryan Sklar of the
Department of the Interior’s Office of the
Solicitor.
Dated: December 22, 2017.
Joseph Balash,
Assistant Secretary—Land and Minerals
Management, U.S. Department of the Interior.
List of Subjects in 43 CFR Part 3160
Administrative practice and
procedure, Government contracts,
Indians-lands, Mineral royalties, Oil and
gas exploration, Penalties, Public landsmineral resources, Reporting and
recordkeeping requirements.
For the reasons stated in the
preamble, and under the authorities
stated below, the Bureau of Land
Management amends 43 CFR part 3160
as follows:
PART 3160—ONSHORE OIL AND GAS
OPERATIONS
1. The authority citation for part 3160
continues to read as follows:
■
Authority: 25 U.S.C. 396d and 2107; 30
U.S.C. 189, 306, 359, and 1751; 43 U.S.C.
1732(b), 1733, and 1740; and Sec. 107, Pub.
L. 114–74, 129 Stat. 599, unless otherwise
noted.
Subpart 3160—Onshore Oil and Gas
Operations: General
2. Revise § 3160.0–3 to read as
follows:
■
§ 3160.0–3
Authority.
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The Mineral Leasing Act, as amended
and supplemented (30 U.S.C. 181 et
seq.), the Act of May 21, 1930 (30 U.S.C.
301–306), the Mineral Leasing Act for
Acquired Lands, as amended (30 U.S.C.
351–359), the Act of March 3, 1909, as
amended (25 U.S.C 396), the Act of May
11, 1938, as amended (25 U.S.C. 396a396q), the Act of February 28, 1891, as
amended (25 U.S.C. 397), the Act of
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May 29, 1924 (25 U.S.C. 398), the Act
of March 3, 1927 (25 U.S.C. 398a-398e),
the Act of June 30, 1919, as amended
(25 U.S.C. 399), R.S. § 441 (43 U.S.C.
1457), the Attorney General’s Opinion
of April 2, 1941 (40 Op. Atty. Gen. 41),
the Federal Property and Administrative
Services Act of 1949, as amended (40
U.S.C 471 et seq.), the National
Environmental Policy Act of 1969, as
amended (40 U.S.C. 4321 et seq.), the
Act of December 12, 1980 (94 Stat.
2964), the Combined Hydrocarbon
Leasing Act of 1981 (95 Stat. 1070), the
Federal Oil and Gas Royalty
Management Act of 1982 (30 U.S.C.
1701), the Indian Mineral Development
Act of 1982 (25 U.S.C. 2102), and Order
Number 3087, dated December 3, 1982,
as amended on February 7, 1983 (48 FR
8983) under which the Secretary
consolidated and transferred the
onshore minerals management functions
of the Department, except mineral
revenue functions and the responsibility
for leasing of restricted Indian lands, to
the Bureau of Land Management.
■ 3. Amend § 3160.0–5 by removing the
definitions of ‘‘Annulus,’’
‘‘Bradenhead,’’ ‘‘Cement Evaluation Log
(CEL),’’ ‘‘Confining zone,’’ ‘‘Hydraulic
fracturing,’’ ‘‘Hydraulic fracturing
fluid,’’ ‘‘Isolating or to isolate,’’ ‘‘Master
hydraulic fracturing plan,’’ ‘‘Proppant,’’
and ‘‘Usable water,’’ and by adding the
definition of ‘‘Fresh water’’ in
alphabetical order to read as follows:
§ 3160.0–5
Definitions.
*
*
*
*
*
Fresh water means water containing
not more than 1,000 ppm of total
dissolved solids, provided that such
water does not contain objectionable
levels of any constituent that is toxic to
animal, plant or aquatic life, unless
otherwise specified in applicable
notices or orders.
*
*
*
*
*
Subpart 3162—Requirements for
Operating Rights Owners and
Operators
4. Amend § 3162.3–2 by revising the
first sentence of paragraph (a) and
revising paragraph (b) to read as follows:
■
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§ 3162.3–2
61949
Subsequent well operations.
(a) A proposal for further well
operations shall be submitted by the
operator on Form 3160–5 for approval
by the authorized officer prior to
commencing operations to redrill,
deepen, perform casing repairs, plugback, alter casing, recomplete in a
different interval, perform water shut
off, commingling production between
intervals and/or conversion to injection.
* * *
(b) Unless additional surface
disturbance is involved and if the
operations conform to the standard of
prudent operating practice, prior
approval is not required for routine
fracturing or acidizing jobs, or
recompletion in the same interval;
however, a subsequent report on these
operations must be filed on Form
3160–5.
*
*
*
*
*
5. Revise § 3162.3–3 to read as
follows:
■
§ 3162.3–3
Other lease operations.
Prior to commencing any operation on
the leasehold which will result in
additional surface disturbance, other
than those authorized under § 3162.3–1
or § 3162.3–2, the operator shall submit
a proposal on Form 3160–5 to the
authorized officer for approval. The
proposal shall include a surface use
plan of operations.
6. Amend § 3162.5–2 by revising the
heading and first sentence of paragraph
(d) to read as follows:
■
§ 3162.5 -2
Control of wells.
*
*
*
*
*
(d) Protection of fresh water and other
minerals. The operator shall isolate
freshwater-bearing and other usable
water containing 5,000 ppm or less of
dissolved solids and other mineralbearing formations and protect them
from contamination. * * *
[FR Doc. 2017–28211 Filed 12–28–17; 8:45 am]
BILLING CODE 4310–84–P
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[Federal Register Volume 82, Number 249 (Friday, December 29, 2017)]
[Rules and Regulations]
[Pages 61924-61949]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2017-28211]
[[Page 61923]]
Vol. 82
Friday,
No. 249
December 29, 2017
Part III
Department of the Interior
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Bureau of Land Management
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43 CFR Part 3160
Oil and Gas; Hydraulic Fracturing on Federal and Indian Lands;
Rescission of a 2015 Rule; Final Rule
Federal Register / Vol. 82 , No. 249 / Friday, December 29, 2017 /
Rules and Regulations
[[Page 61924]]
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DEPARTMENT OF THE INTERIOR
Bureau of Land Management
43 CFR Part 3160
[LLWO300000 L13100000 PP0000 18X]
RIN 1004-AE52
Oil and Gas; Hydraulic Fracturing on Federal and Indian Lands;
Rescission of a 2015 Rule
AGENCY: Bureau of Land Management, Interior.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: On March 26, 2015, the Bureau of Land Management (BLM)
published in the Federal Register a final rule entitled, ``Oil and Gas;
Hydraulic Fracturing on Federal and Indian Lands'' (2015 rule). With
this final rule, the BLM is rescinding the 2015 rule because we believe
it imposes administrative burdens and compliance costs that are not
justified. This final rule returns the affected sections of the Code of
Federal Regulations (CFR) to the language that existed immediately
before the published effective date of the 2015 rule (June 24, 2015),
except for changes to those regulations that were made by other rules
published between the date of publication of the 2015 rule and now, and
the phrase ``perform nonroutine fracturing jobs,'' which is not
restored to the list of subsequent operations requiring prior approval.
None of the changes by other rules are relevant to this rulemaking.
DATES: This final rule is effective on December 29, 2017.
FOR FURTHER INFORMATION CONTACT: Lorenzo Trimble, Acting Division
Chief, Fluid Minerals Division, 202-912-7342, for information regarding
the substance of this final rule or information about the BLM's Fluid
Minerals program. Persons who use a telecommunications device for the
deaf (TDD) may call the Federal Relay Service (FRS) at 1-800-877-8339,
24 hours a day, 7 days a week, to leave a message or question with the
above individuals. You will receive a reply during normal hours.
SUPPLEMENTARY INFORMATION:
Executive Summary
Pursuant to the Mineral Leasing Act (MLA), the Federal Land Policy
and Management Act (FLPMA), the Indian mineral leasing laws, and other
legal authorities, the BLM is charged with administering oil and gas
operations on Federal and Indian lands in a manner that allows for
responsible and appropriate resource development. This final rule is
needed to prevent the unnecessarily burdensome and unjustified
administrative requirements and compliance costs of the 2015 rule from
encumbering oil and gas development on Federal and Indian lands.
The process known as ``hydraulic fracturing'' has been used by the
oil and gas industry since the 1950s to stimulate production from oil
and gas wells. In recent years, public awareness of the use of
hydraulic fracturing practices has grown. New horizontal drilling
technology has allowed increased access to oil and gas resources in
tight shale formations across the country, sometimes in areas that have
not previously experienced significant oil and gas development. As
hydraulic fracturing has become more common, public concern increased
about whether hydraulic fracturing contributes to or causes the
contamination of groundwater sources, whether the chemicals used in
hydraulic fracturing should be disclosed to the public, and whether
there is adequate management of well integrity and of the ``flowback''
fluids that return to the surface during and after hydraulic fracturing
operations.
On March 26, 2015, the BLM published in the Federal Register a
final rule entitled, ``Oil and Gas; Hydraulic Fracturing on Federal and
Indian Lands'' (80 FR 16128) (2015 rule). The 2015 rule was intended
to: Ensure that wells are properly constructed to protect water
supplies, make certain that the fluids that flow back to the surface as
a result of hydraulic fracturing operations are managed in an
environmentally responsible way, and provide public disclosure of the
chemicals used in hydraulic fracturing fluids. To achieve its
objectives, the 2015 rule required oil and gas operators to:
Obtain the BLM's approval before conducting hydraulic
fracturing operations by submitting an application with information and
a plan for the hydraulic fracturing design (43 CFR 3162.3-3(d)(4)).
Include a hydraulic fracturing application in applications
for permits to drill (APDs), or in a subsequent ``sundry notice'' (43
CFR 3162.3-3(c)).
Include information about the proposed source of water in
each hydraulic fracturing application so that the BLM can complete
analyses required by the National Environment Policy Act (NEPA) (43 CFR
3162.3-3(d)(3)).
Include available information about the location of nearby
wells to help prevent ``frack hits'' (i.e., unplanned surges of
pressurized fluids into other wells that can damage the wells and
equipment and cause surface spills) (43 CFR 3162.3-3(d)(4)(iii)(C)).
Verify that the well casing is surrounded by adequate
cement, and test the well to make sure it can withstand the pressures
of hydraulic fracturing (43 CFR 3162.3-3(e)(1) and (2) and (f)).
Isolate and protect usable water, while redefining
``usable water'' to expressly defer to classifications of groundwater
by states and tribes, and the Environmental Protection Agency, 43 CFR
3160.0-7; and require demonstrations of 200 feet of adequate cementing
between the fractured formation and the bottom of the closest usable
water aquifer, or cementing to the surface (43 CFR 3162.3-3(e)(2)(i)
and (ii)).
Monitor and record the annulus pressure during hydraulic
fracturing operations, and report significant increases of pressure (43
CFR 3162.3-3(g)).
File post-fracturing reports containing information about
how the hydraulic fracturing operation actually occurred (43 CFR
3162.3-3(i)).
Submit lists of the chemicals used (non-trade-secrets) to
the BLM by sundry notice (Form 3160-5), to FracFocus (a public website
operated by the Ground Water Protection Council and the Interstate Oil
and Gas Compact Commission), or to another BLM-designated database (43
CFR 3162.3-3(i)(1)).
Withhold trade secret chemical identities only if the
operator or the owner of the trade secret submits an affidavit
verifying that the information qualifies for trade secret protection
(43 CFR 3162.3-3(j)).
Obtain and provide withheld chemical information to the
BLM, if the BLM requests the withheld information (43 CFR 3162.3-
3(j)(3)).
Store recovered fluids in above-ground rigid tanks of no
more than 500-barrel capacity, with few exceptions, until the operator
has an approved plan for permanent disposal of produced water (as
required by Onshore Oil and Gas Order No. 7) (43 CFR 3162.3-3(h)).
The 2015 rule also authorized two types of variances:
Individual operation variances to account for local
conditions or new or different technology (43 CFR 3162.3-3(k)(1)).
State or tribal variances to account for regional
conditions or to align the BLM requirements with state or tribal
regulations (43 CFR 3162.3-3(k)(2)).
For either type of variance to be approved, the variance needed to
meet or exceed the purposes of the specific provision of the 2015 rule
for which the
[[Page 61925]]
variance is being granted (43 CFR 3162.3-3(k)(3)).
The 2015 rule was immediately challenged in court. The United
States District Court for the District of Wyoming stayed the 2015 rule
before it went into effect, and later issued a final order setting
aside the rule, concluding that it was outside the BLM's statutory
authority. On appeal, the United States Court of Appeals for the Tenth
Circuit dismissed the appeal as prudentially unripe, and vacated the
District Court's final order with instructions for the District Court
to dismiss the case without prejudice. The plaintiffs have moved for
rehearing or reconsideration en banc. Briefing on those petitions is
complete. The Tenth Circuit has not yet issued its mandate to the
District Court, and thus the 2015 rule has not gone into effect.
Commenters and a District Court have raised doubts about BLM's
statutory authority to regulate hydraulic fracturing operations on
Federal and Indian lands. The BLM believes that it is not only better
policy to rescind the 2015 rule to relieve operators of duplicative,
unnecessary, costly and unproductive regulatory burdens, but it also
eliminates the need for further litigation about BLM's statutory
authority.
On March 28, 2017, President Trump issued Executive Order 13783,
entitled, ``Promoting Energy Independence and Economic Growth'' (82 FR
16093, Mar. 31, 2017), which directed the Secretary of the Interior to
review four specific rules, including the 2015 rule, for consistency
with the policy set forth in section 1 of the Order and, if
appropriate, take action to lawfully suspend, revise, or rescind those
rules that are inconsistent with the policy set forth in Executive
Order 13783.
Section 1 of Executive Order 13783 states that it is in the
national interest to promote clean and safe development of United
States energy resources, while avoiding ``regulatory burdens that
unnecessarily encumber energy production, constrain economic growth,
and prevent job creation.'' Section 1 states that the prudent
development of these natural resources is ``essential to ensuring the
Nation's geopolitical security.'' Section 1 finds that it is in the
national interest to ensure that electricity is affordable, reliable,
safe, secure, and clean, and that coal, natural gas, nuclear material,
flowing water, and other domestic sources, including renewable sources,
can be used to produce it.
Accordingly, Section 1 of Executive Order 13783 declares that the
policy of the United States is that: (1) Executive departments and
agencies immediately review regulations that potentially burden the
development or use of domestically produced energy resources and, as
appropriate, suspend, revise, or rescind those that unduly burden
domestic energy resources development ``beyond the degree necessary to
protect the public interest or otherwise comply with the law''; and (2)
To the extent permitted by law, agencies should promote clean air and
clean water, while respecting the proper roles of the Congress and the
States concerning these matters; and (3) Necessary and appropriate
environmental regulations comply with the law, reflect greater benefit
than cost, when permissible, achieve environmental improvements, and
are developed through transparent processes using the best available
peer-reviewed science and economics.
To implement Executive Order 13783, Secretary of the Interior Ryan
K. Zinke issued Secretarial Order No. 3349 entitled, ``American Energy
Independence,'' on March 29, 2017, which, among other things, directed
the BLM to proceed expeditiously in proposing to rescind the 2015 rule.
As directed by Executive Order 13783 and Secretarial Order No.
3349, the BLM conducted a review of the 2015 rule. As a result of this
review, the BLM believes that the compliance costs associated with the
2015 rule are not justified.
In conjunction with its review of the 2015 rule, the BLM analyzed
the potential economic implications of implementing the 2015 rule and
this final rule that rescinds the 2015 rule. That analysis is
documented in the regulatory impact analysis (RIA) document that the
BLM prepared for this final rule. As described in detail in that RIA,
the BLM has estimated that this final rule will provide a reduction in
compliance costs relative to the 2015 rule of up to $9,690 per well or
approximately $14 million to $34 million per year.
When issuing the 2015 rule, the BLM acknowledged that it already
had ``an extensive process in place to ensure that operators conduct
oil and gas operations in an environmentally sound manner'' and that
``the regulations and Onshore Orders that have been in place to this
point have served to provide reasonable certainty of environmentally
responsible development of oil and gas resources'' (80 FR at 16133 and
16137). However, in the RIA for the 2015 rule, while noting that many
of the requirements of the 2015 rule were consistent with industry
practice and that some were duplicative of state requirements or were
generally addressed by existing BLM requirements, the BLM asserted that
the 2015 rule would provide additional assurance that operators are
conducting hydraulic fracturing operations in an environmentally sound
and safe manner, and increase the public's awareness and understanding
of these operations.
While the extent of the benefits that the additional assurances
might provide are questionable, it follows that the rescission of the
2015 rule could potentially reduce any such assurances. However,
considering state regulatory programs, the sovereignty of tribes to
regulate operations on their lands, and the pre-existing Federal
regulations, the proposed rescission of the 2015 rule would not leave
hydraulic fracturing operations unregulated.
The BLM's review of the 2015 rule also included a review of state
laws and regulations that found that most states are either currently
regulating hydraulic fracturing or are in the process of establishing
hydraulic fracturing regulations. When the 2015 rule was issued, 20 of
the 32 states with currently existing Federal oil and gas leases had
regulations addressing hydraulic fracturing. In the time since the
promulgation of the 2015 rule, an additional 12 states have introduced
laws or regulations addressing hydraulic fracturing. As a result, all
32 states with Federal oil and gas leases currently have laws or
regulations that address hydraulic fracturing operations.\1\ In
addition, some tribes with oil and gas resources have also taken steps
to regulate oil and gas operations, including hydraulic fracturing, on
their lands.
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\1\ The reference to 32 states with existing Federal oil and gas
leases includes the following states: Alabama, Alaska, Arizona,
Arkansas, California, Colorado, Idaho, Illinois, Indiana, Kansas,
Kentucky, Louisiana, Maryland, Michigan, Mississippi, Montana,
Nebraska, Nevada, New Mexico, New York, North Dakota, Ohio,
Oklahoma, Oregon, Pennsylvania, South Dakota, Tennessee, Texas,
Utah, Virginia, West Virginia, and Wyoming. The State of Oregon
regulates hydraulic fracturing operations by way of its regulations
addressing ``Water Injection and Water Flooding of Oil and Gas
Properties'' (Oregon Administrative Rules [Or. Admin. R.] sec. 632-
010-0194). The State of Arizona regulates hydraulic fracturing
operations under regulations addressing ``Artificial Stimulation of
Oil and Gas Wells'' (Arizona Administrative Code [A.A.C.] sec. R12-
7-117). The State of Indiana issued ``emergency rules'' in 2011 and
2012 that incorporated new legislation addressing hydraulic
fracturing (Pub. L. 140-2011 and Pub. L. 16-2012) into Indiana's oil
and gas regulations at 312 Indiana Administrative Code (IAC) Article
16. For further information about the state regulatory programs, see
Sec. 2.12 of the RIA and Appendix 1 of the EA prepared for this
rule.
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The BLM also now believes that disclosure of the chemical content
of hydraulic fracturing fluids to state regulatory agencies and/or
databases
[[Page 61926]]
such as FracFocus is more prevalent than it was in 2015 and, therefore,
there is no continuing need for a Federal chemical disclosure
requirement, since companies are already making those disclosures on
most operations, either to comply with state law or voluntarily. There
are 25 states that currently use FracFocus for chemical disclosures.
These include seven states where the BLM has major oil and gas
operations, including Colorado, Montana, New Mexico, North Dakota,
Oklahoma, Texas, and Utah.
In addition to state and tribal regulation of hydraulic fracturing,
the BLM has several pre-existing regulations that it will continue to
rely on, some of which are set out at 43 CFR subpart 3162 and in
Onshore Oil and Gas Orders 1, 2, and 7. These regulations ensure that
operators conduct oil and gas operations in an environmentally sound
manner and also reduce the risks associated with hydraulic fracturing
by providing specific requirements for well permitting; construction,
casing, and cementing; and disposal of produced water.\2\ The BLM also
possesses discretionary authority allowing it to impose site-specific
protective measures reducing the risks associated with hydraulic
fracturing.
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\2\ Additional discussion regarding Onshore Oil and Gas Orders
1, 2, and 7, and 43 CFR subpart 3162, is provided in Sec. 2.11 of
the RIA and the EA prepared for this rule.
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Prior to the 2015 rule, the regulations at 43 CFR 3162.3-2(a)
(2014) provided in pertinent part that a ``proposal for further well
operations shall be submitted by the operator on Form 3160-5 for
approval by the authorized officer prior to commencing operations to .
. . perform nonroutine fracturing jobs . . . .'' In the proposed rule
that preceded this final rule, the BLM offered to restore the
regulatory text in Sec. 3162.3-2(a) regarding ``nonroutine fracturing
jobs'' to exactly as it existed in the pre-2015 rule regulations. Those
regulations, however, did not define ``nonroutine fracturing jobs'' or
provide guidance to operators or BLM authorized officers on how to
distinguish ``routine'' from ``nonroutine.'' Some of the comments that
were submitted for the proposed rule noted this and criticized the
regulations for being vague, confusing, and difficult for operators and
the BLM to apply. In light of these comments, the BLM reconsidered its
initial proposal to restore the regulation text in section 3162.3-2(a)
requiring prior approval for ``nonroutine fracturing jobs.''
As a result of considerable advances in oil and gas development
technology in the last 20 years, hydraulic fracturing practices that
would have been considered ``nonroutine'' when the BLM originally
issued the regulations requiring prior approval for ``nonroutine
fracturing jobs'' are now commonly utilized and considered ``routine.''
The combination of advances in oil and gas development technology and
the BLM's existing authority to mitigate the potential risks of
hydraulic fracturing operations through site-specific protective
measures that are applied as a part of the environmental review and
approval process at the APD stage has made post-APD approvals for
``nonroutine fracturing jobs'' at most a very rare occurrence. In fact,
while the BLM has not been tracking requests for approval of
``nonroutine fracturing jobs,'' recent inquiries to BLM state offices
have not revealed any examples of ``nonroutine fracturing'' requests or
approvals. Thus, given that the ``nonroutine fracturing'' requirement
has not, and does not seem to serve any purpose, and removing it from
the regulations could reduce the potential for unproductive confusion
or paperwork without adverse effects, the BLM has not restored the
``nonroutine fracturing'' requirement in this final rule.
The BLM's review of the 2015 rule also included a review of
incident reports from Federal and Indian wells since December 2014.
This review indicated that resource damage is unlikely to increase by
rescinding the 2015 final rule because of the rarity of adverse
environmental impacts that occurred from hydraulic fracturing
operations since promulgation of the 2015 rule. The BLM now believes
that the appropriate framework for mitigating these impacts exists
through state regulations, through tribal exercise of sovereignty, and
through BLM's own pre-existing regulations and authorities (pre-2015
rule 43 CFR subpart 3162 and Onshore Orders 1, 2, and 7).
I. Background
II. Discussion of the Final Rule and Comments on the Proposed Rule
III. Procedural Matters
I. Background
The development and production of oil and gas, including hydraulic
fracturing operations, are regulated under a framework of Federal,
state, and local laws, and, on some tribal lands, by tribal
regulations. Several Federal agencies implement Federal laws and
requirements while each state in which oil and gas is produced has one
or more regulatory agencies that administer state laws and
requirements.
State and local laws apply on Federal lands, except to the extent
that they are preempted by Federal law. Federal preemption is rare, and
is not at issue in the final rule. Accordingly, the drilling and
completion of oil and gas wells, including hydraulic fracturing
operations, are subject to Federal and state and local regulation on
Federal lands. If the requirements of a state regulation are more
stringent than those of a Federal regulation, for example, the operator
can comply with both the state and the Federal regulation by meeting
the more stringent state requirement.
Tribal and Federal laws apply to oil and gas drilling and
completion operations, including hydraulic fracturing operations, on
tribal lands. Operators on tribal lands can comply with both tribal and
Federal regulations governing drilling and completion requirements by
complying with the stricter of those rules.
Regardless of any difference in operational regulations, operators
on Federal lands must comply with all Federal, state, and local
permitting and reporting requirements. On Indian lands, they must
comply with all Federal and tribal permitting and reporting
requirements.
Existing BLM Requirements--Not Affected by This Final Rule
The BLM has an extensive process in place to ensure that operators
conduct oil and gas operations in a safe and environmentally sound
manner that protects resources. The following discussion provides a
description of some of the BLM's existing processes and requirements
that are not affected by the rescission of the 2015 rule pursuant to
this final rule that help to ensure that the risks of oil and gas
operations, including hydraulic fracturing, are appropriately
minimized.
The BLM applies a tiered decision-making approach when providing
access for the development of Federal oil and gas resources on public
lands. First, the BLM develops land use plans (the BLM refers to these
plans as Resource Management Plans, or RMPs). The RMP serves as the
basis for all land use decisions the BLM makes, including decisions to
delineate public lands that are appropriate for oil and gas leasing.
Establishment or revision of an RMP requires preparation of an
environmental impact statement (EIS) in accordance with the National
Environmental Policy Act (NEPA). In areas where lands are open for oil
and gas leasing, the EIS prepared to support establishment or revision
of the RMP analyzes oil and gas development related impacts that may be
expected to
[[Page 61927]]
occur over the life of an RMP (typically 20 years). The RMP identifies
the terms and conditions under which the BLM would allow oil and gas
development to occur in order to protect other resource values. Those
terms and conditions may include mitigation measures that would be
evaluated through the EIS and are implemented as stipulations
incorporated into oil and gas leases. If necessary, certain lands are
closed to oil and gas leasing altogether when such use is incompatible
with sensitive resources or other planned uses. In addition to
compliance with NEPA, the BLM must comply with the National Historic
Preservation Act (NHPA), the Endangered Species Act (ESA), and other
applicable Federal laws and regulations. Once an RMP has been approved,
the BLM makes land use decisions, including oil and gas development
decisions, in accordance with the RMP, or any revisions or amendments
to that RMP.
Before oil and gas activities may occur on Federal lands,
interested parties must obtain a lease from the BLM. Oil and gas leases
are acquired through an auction-style sale process in which interested
parties typically identify tracts of land that they would like to see
leased. The BLM will conduct a preliminary evaluation to first
determine whether the lands nominated for oil and gas leasing are under
Federal jurisdiction and are open to leasing in accordance with the
applicable RMP. The BLM will then conduct a second tier of NEPA
review--typically through an EA--to address potential impacts that
could be caused by oil and gas development within the nominated lease
area. The NEPA review conducted at the leasing stage tiers to the EIS
prepared for the RMP. If the BLM's analysis determines that the
nominated tracts are suitable for leasing, the BLM would offer the
tracts for lease during a competitive oil and gas lease sale auction.
If any of the tracts are not bid upon during the lease sale auction,
those tracts become available for non-competitive leasing by the first
qualified applicant for a two year period that begins on the first
business day following the last day of the lease sale. In addition to
compliance with the NEPA, the BLM also complies with the NHPA and the
ESA at the leasing stage. Upon issuance by the BLM, the lease allows
the operator to conduct operations on the lease subject to the
requirements of existing regulations, the lease terms and stipulations,
and the requirement that the operator obtain BLM approval of a site-
specific Application for Permit to Drill (APD).
When trust or restricted Indian lands are involved, the tribe or
individual Indian mineral owner plans the uses of their own lands. They
lease their own oil and gas resources with the consent of the
Department of the Interior's (``DOI'' or ``the Department'') Bureau of
Indian Affairs (BIA). Nonetheless, the BLM often serves as a
cooperating agency during the development of the environmental review
for such actions. Moreover, pursuant to delegations from the Secretary
of the Interior (Secretary) and BIA regulations, the BLM regulates oil
and gas operations on trust and restricted Indian lands, applying the
same operating regulations that apply on Federal lands.
The procedures followed when issuing leases to develop Indian oil
and gas resources may be similar to, or different from, the leasing
process used for Federal lands, depending upon a number of different
factors. For example, when tribal oil and gas resources are leased
under the authority of the Indian Mineral Leasing Act of 1938 (IMLA),
the BIA typically conducts a competitive lease sale process that shares
many similarities with the leasing process for Federal lands. In
contrast, the Indian Mineral Development Act of 1982 (IMDA), allows
Indian mineral owners to forego the competitive auction-style leasing
process and negotiate directly with potential operators for agreements
to develop their oil and gas resources.\3\ However, for both IMLA and
IMDA authorized leases and agreements, the approval of the Indian
mineral owner and the BIA or the DOI is required.\4\ Much like with oil
and gas leasing actions involving Federal lands, authorizations
pursuant to the IMLA and the IMDA to develop Indian oil and gas
resources are subject to compliance with applicable Federal statutes,
including NEPA. The procedures for issuing leases and other development
agreements for Indian oil and gas resources are outlined in the BIA's
regulations at 25 CFR parts 211 (IMLA leasing), 212 (agreements for
allotted lands), and 225 (IMDA agreements).
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\3\ The IMDA authorizes Indian tribes and individual Indian
mineral owners to enter into leases, as well as other types of
agreements, to explore for and develop their oil and gas resources.
25 U.S.C. 2102(a). Indian allotted lands may also be leased for
mineral development pursuant to 25 U.S.C. 396.
\4\ In certain situations, IMDA agreements may only be approved
by the Secretary of the Interior or the Assistant Secretary for
Indian Affairs. See 25 U.S.C. 2103(d) and 25 CFR 225.3.
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The BLM has existing regulations, including Onshore Oil and Gas
Orders, to ensure that operators conduct oil and gas exploration and
development in a safe and environmentally responsible manner that
protects other resources. Sections 3162.3-1 and Onshore Order 1 require
an operator to get approval from the BLM prior to drilling a well. The
operator must submit an APD containing all of the information required
by Onshore Order 1. This includes a completed Form 3160-3, Application
for Permit to Drill or Re-Enter, a well plat, a drilling plan, a
surface use plan, bonding information, and an operator certification.
Upon receiving a drilling proposal on Federal lands, the BLM is
required by existing section 3162.3-1(g) to post information for public
inspection for at least 30 days before the BLM can approve the APD. The
information must include: The company/operator name; the well name/
number; and the well location described to the nearest quarter-quarter
section (40 acres), or similar land description in the case of lands
described by metes and bounds, or maps showing the affected lands and
the location of all tracts to be leased and of all leases already
issued in the general area.
The public can review the posted information and provide any input
they would like the BLM to consider during the environmental analysis
the BLM prepares prior to making a decision on the APD.
The drilling plan provided by the operator must be in sufficient
detail to permit the BLM to complete an appraisal of the technical
adequacy of, and environmental effects associated with, the proposed
project. The operator must provide geological information, including
the name and estimated tops of all geologic groups, formations,
members, and zones. The operator must also provide the estimated depths
and thickness of formations, members, or zones potentially containing
usable water, oil, gas, or prospectively valuable deposits of other
minerals that the operator expects to encounter, and their plans for
protecting such resources. The BLM uses this information and the BLM's
geologists' and engineers' professional reviews to ensure that usable
water zones are protected.
The operator must provide minimum specifications for blowout
prevention equipment that they will use to keep control of well
pressures encountered while drilling. The BLM evaluates the proposed
equipment to determine that it is adequate for anticipated pressures
that the well may encounter in order to prevent loss of control of the
well and potential environmental issues. The operator must provide a
proposed casing program, including the size, grade, weight, and setting
depth of each
[[Page 61928]]
casing string. The BLM engineers evaluate the proposed casing to ensure
that it is being set at proper depths to protect other resources,
including usable water. The BLM engineers also ensure that the casing
size and strength is sufficient for the depths at which it will be set,
and the pressures that the well will encounter.
The operator must provide information regarding the proposed
cementing program. This includes the amount and types of cement the
operator will use for each casing string, and the expected top of
cement for each casing string. The cement is critical for the isolation
and protection of usable water since it is the cement that establishes
a barrier outside the casing between any hydrocarbon bearing zones and
usable water zones. The proposed cementing program is the first step
for this protection. The BLM engineers evaluate the proposed cementing
program to ensure that the volume and strength of the cement is
adequate to achieve the desired protections.
The operator must include in the drilling plan information
regarding their proposed drilling fluid. The operator must provide the
type and characteristics of the proposed circulating medium for
drilling each well bore section, including the quantities and types of
mud the operator will maintain, and the monitoring equipment the
operator will utilize on the circulating system. The BLM engineers
review this information to ensure that the drilling fluid system and
additives will be compatible and not detrimental to all usable water
and prospectively valuable mineral zones that the well bore may
encounter. The operator must also provide their proposed testing,
logging, and coring procedures. This may include resistivity, gamma
ray, spontaneous potential, caliper, and neutron logs as well as cement
evaluation logs. The BLM reviews the proposed logging suite and
determines if the operator will need to run any additional logs to
provide additional downhole information.
The operator's drilling plan must address the expected bottom-hole
pressure and any anticipated abnormal pressures, temperatures, or
potential hazards that the well may encounter. Hazards may include lost
circulation zones, hydrogen sulfide zones, or faults and fractures. The
operator must also include a plan for mitigating such hazardous. The
BLM geologists review this information to determine if any other
anticipated hazards exist. The BLM engineers review this information to
ensure the proposed mitigation to address any anticipated hazards is
adequate.
The operator must include in its drilling plan any other
information regarding the proposed operation that it would like the BLM
to consider. This might include, but is not limited to, the directional
drilling plan for deviated or horizontal wells, which would provide the
proposed wellbore path. The BLM engineers review the proposed
directional plan to ensure there will not be any potential issues with
existing wells.
The operator's APD must also include a surface use plan of
operations, or the equivalent required by another surface management
agency. The surface use plan must contain sufficient details of the
proposed surface use to provide for safe operations, adequate
protection of the surface resources, groundwater, and other
environmental components. The operator must also describe any Best
Management Practices (BMP) they plan to use. BMPs are state-of-the-art
mitigation measures applied to oil and natural gas drilling and
production to help ensure that operators conduct energy development in
an environmentally responsible manner. BMPs can protect water,
wildlife, air quality, or landscapes. The BLM encourages operators to
incorporate BMPs into their plans.
The operator's surface use plan should follow the BLM's Surface
Operating Standards and Guidelines for Oil and Gas Exploration and
Development, which is commonly referred to as The Gold Book.\5\ The BLM
developed The Gold Book to assist operators by providing information on
the requirements for obtaining permit approval and conducting
environmentally responsible oil and gas operations.
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\5\ The Gold Book is available on the BLM's website, at: https://www.blm.gov/programs/energy-and-minerals/oil-and-gas/operations-and-production/the-gold-book.
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The operator's surface use plan must include information regarding
existing roads they plan to use to access the proposed well location
and must explain how they will improve or maintain existing roads. The
surface use plan must also include the operator's plan for any new
access roads they plan to build. The operator must design roads based
upon the type of road, the safety requirements, traffic
characteristics, environmental conditions, and the type of vehicles
that will use the road. The proposed road description must include:
Road width, maximum grade, crown design, turnouts, drainage and ditch
design, on-site and off-site erosion control, revegetation of disturbed
areas, location and size of culverts and/or bridges, fence cuts and/or
cattleguards, major cuts and fills, source and storage of topsoil, and
the type of surface materials that the operator will use.
The operator must include a map showing all known wells, regardless
of well status (producing, abandoned, etc.) within a one-mile radius of
the proposed location. The BLM uses this information to ensure the
proposal does not conflict with any current surface use. The BLM uses
this well information to identify any potential downhole conflicts or
issues between the existing wells and the proposed well. If the BLM
does identify conflicts, the BLM will require the operator to modify
their proposal or to submit plans to mitigate the issue.
The operator must include a map or diagram that shows the location
of all production facilities and lines they will install if the well is
successful (i.e., a producing well), as well as any existing
facilities. This would include all buried oil, water, or gas pipelines
and all overhead and buried power lines. The BLM reviews this
information to identify any potential conflicts with the proposed
facilities.
The operator must include in their surface use plan information
concerning the water supply, such as rivers, creeks, springs, lakes,
ponds, and wells that the operator plans to use for drilling the well.
This may or may not be the same source of water the operator plans to
use for their hydraulic fracturing operations. The BLM does not
regulate water usage, but the BLM does use the information about water
supply in conducting the environmental analysis of the APD. The BLM
uses the information to determine if the operator must obtain any
additional approvals such as a right-of-way across Federal lands that
may be necessary for the transport of water.
The operator must include a written description of the methods and
locations it proposes for safe containment and disposal of each type of
waste material (e.g., cuttings, garbage, salts, chemicals, sewage,
etc.) that results from drilling the proposed well. The narrative must
include plans for the eventual disposal of drilling fluids and any
produced oil or water recovered during testing operations. The operator
must describe plans for the construction and lining, if necessary, of
the reserve pit.
The surface use plan must include the character, intended use, and
source of all construction materials, such as sand, gravel, stone, and
soil material. The operator must identify the location and construction
method and materials from
[[Page 61929]]
all anticipated ancillary facilities such as camps, airstrips, and
staging areas. This information will be used to assess the
environmental impacts of the proposed operations.
The operator must include a diagram of the proposed well site
layout. The layout must show the location and orientation of the
following: The proposed drill pad, the reserve pit/blooie line/flare
pit location, access road entry points, and the reserve pit showing all
cuts and fills, the drilling rig, any dikes and ditches to be
constructed, and topsoil and/or spoil material stockpiles.
The operator must submit a plan for the surface reclamation or
stabilization of all disturbed areas. The plan must address interim
(during production) post-drilling reclamation for the area of the well
pad not needed for production, as well as final abandonment of the
location. The plan must include, as appropriate, the following:
Configuration of the reshaped topography, drainage systems, segregation
of stockpiles, surface disturbances, backfill requirements, proposals
for pit closures, redistribution of topsoil, soil treatments, seeding
or other steps to reestablish vegetation, weed control, and practices
necessary to reclaim all disturbed areas, including any access roads
and pipelines.
If the BLM does not manage the surface, the surface management
agency must approve the surface use plan according to their respective
regulations and guidance documents.
The APD must provide proof of adequate bond coverage as required by
existing 43 CFR 3104.1 for Federal lands and by 25 CFR 211.24, 212.24,
and 225.30, for Indian lands. These regulations require the operator or
the lessee to have an adequate bond in place prior to the BLM's
approval of the APD. If the BLM determines that the current bond amount
is not sufficient, the BLM can require additional bond coverage. The
BLM determines the need for bond increases by considering the
operator's history of previous violations, the location and depth of
wells, the total number of wells involved, the age and production
capability of the field, and any unique or unusual conditions in the
planned drilling operations or in the surrounding environment.
Upon receipt of a complete APD, the BLM will schedule an onsite
inspection with the operator. The purpose of the onsite inspection is
for the BLM and operator to further identify site-specific resource
concerns and requirements not originally identified during the
application stage. Prior to, or in conjunction with, the onsite
inspection, the BLM or other surface management agency will advise the
operator if any special inventories or studies are required, such as
for cultural resources or threatened and endangered species.
The onsite inspection team will include the BLM, a representative
of any other surface management agency, the operator or permitting
agent, and other parties associated with planning work on the project,
such as the operator's principal dirtwork contractor, agency resource
specialists, surveyors, and pipeline or utility company
representatives. When the onsite inspection is on private surface, the
BLM will invite the surface owner to attend. The purpose of the onsite
inspection is to discuss the proposal; determine the best location for
the well, road, and facilities; identify site-specific concerns and
potential environmental impacts associated with the proposal; and
discuss the conditions of approval (COA) or possible environmental
BMPs. If the BLM identifies resource conflicts, the BLM has the
authority to require the operator to move surface facilities to
locations that would reduce resource impacts while still allowing
development of the leased minerals.
After the BLM has reviewed the operator's proposed plans and
conducted the onsite inspection, the BLM will prepare an environmental
impacts analysis document in conformance with the requirements of NEPA,
and the Department of the Interior's regulations. The extent of the
environmental analysis process and the time period for issuance of a
decision on the APD will depend upon the complexity of the proposed
action and resulting analysis, the significance of the environmental
effects disclosed, and the completion of appropriate consultation
processes. In each case, the environmental analysis considers
environmental concerns and resource issues in the area, including those
the BLM or operator identified during the onsite inspection, such as
potentially impacted cultural resources, endangered species, surface
water, ground water, and other natural resources. A group of resource
specialists conduct the analysis. The composition of the team depends
on the resource issues in that area and any resource issues that the
BLM or operator identified during the onsite inspection. The resource
specialists may include petroleum engineers, geologists, natural
resources specialists, wildlife biologists, archeologists,
hydrologists, soil scientists, botanists, recreation specialists, range
management specialists, and realty specialists.
The environmental analysis may be conducted for a single well, a
group of wells, or for an entire field. The public is welcome to
provide input to the BLM for inclusion in the analysis. The BLM posts
notices of all Federal APDs for public inspection in the authorizing
office and on the internet. For large projects, such as field
development environmental assessments or environmental impact
statements, the BLM will go through public scoping and will issue a
draft analysis for public comment prior to completing the final
analysis and issuing a decision.
The environmental analysis will identify potential impacts from the
proposed action. The BLM will develop any necessary COAs to mitigate
those potential impacts. If the BLM identifies unacceptable impacts,
the BLM will ask the operator to modify its proposal, or the BLM may
deny the application. The BLM will attach the COAs to the approved APD.
The operator must follow the approved plan and all COAs.
Upon BLM's approval of an APD, the operator may commence drilling
of the well. In addition to the approved plan and the COAs attached to
the APD, the operator must also comply with the requirements of Onshore
Order 2. Onshore Order 2 details the BLM's uniform national minimum
standards of performance expected from operators when conducting
drilling operations on Federal and Indian lands. Many of the
requirements of Onshore Order 2 ensure the protection of usable water.
Onshore Order 2 defines ``isolating'' as ``using cement to protect,
separate, or segregate usable water and mineral resources'' and
``usable water'' as ``generally those waters containing up to 10,000
ppm of total dissolved solids.''
Onshore Order 2 requires that the operator conduct the proposed
casing and cementing programs as approved to protect and/or isolate all
usable water zones, lost circulation zones, abnormally pressured zones,
and any prospectively valuable deposits of minerals. It requires that
the operator determine the casing setting depths based on all relevant
factors, including: Presence/absence of hydrocarbons; fracture
gradients; usable water zones; formation pressures; lost circulation
zones; other minerals; or other unusual characteristics. It also
requires the operator to report all indications of usable water.
Onshore Order 2 requires the operator to run centralizers on the
bottom 3 joints of surface casing to help ensure the casing is centered
in the drilled hole prior to cementing. This helps to ensure wellbore
integrity. It also requires the operator to cement the surface casing
[[Page 61930]]
back to the surface either during the primary cement job or by remedial
cementing. Cementing the surface casing back to the surface ensures
that all usable water zones behind the surface casing are isolated and
protected. Onshore Order 2 requires the operator to wait until the
cement for all casing strings achieves a minimum of 500 psi compressive
strength at the casing shoe prior to drilling out the casing shoe. It
requires the operator to use top plugs during cementing operations to
reduce contamination of the cement by displacement fluid. It requires
the operator to use a bottom plug or other acceptable technique, such
as a preflush fluid, inner string cement method, etc., to help isolate
the cement from contamination by the mud fluid being displaced ahead of
the cement slurry. By using proper cementing techniques such as these,
the operator can complete the cement job as planned and thus protect
usable water.
Onshore Order 2 requires the operator to pressure test the casing
prior to drilling out the casing shoe. This test ensures the integrity
of the casing. Onshore Order 2 requires the operator to conduct a
pressure integrity test of each casing shoe on all exploratory wells,
and on that portion of any well approved for a 5000 psi blowout
preventer. The operator must conduct this test before drilling 20 feet
of new hole. The pressure test ensures the integrity of the cement
around the casing shoe.
Onshore Order 2 identifies the minimum requirements for blowout
prevention equipment and the minimum standards for testing the
equipment. Proper sizing, installation, and testing of the blowout
prevention equipment ensures that the operator maintains control of the
well during the drilling process, which is necessary for protection of
usable water zones.
The BLM conducts inspections of drilling operations to ensure that
operators comply with the Onshore Order 2 drilling regulations, the
approved APD, and the associated COAs. The BLM drilling inspections
consist of two general types of inspections: Technical and
environmental. The BLM petroleum engineering technicians conduct
technical inspections of the drilling operations, such as witnessing
the running and cementing of the casing, witnessing the testing of the
blowout prevention equipment, and detailed drilling rig inspections
that include review of documentation such as the third party cementing
job ticket, which describes the cementing operation including the type
and amount of cement used, the cement pump pressures, and the
observation of cement returns to the surface, if applicable. Through
witnessing the operation or the review of the documentation, the BLM
inspectors verify that the drilling operations are conducted in
accordance with the approved plan and that no wellbore issues exist.
The BLM natural resource specialists conduct environmental inspections
of drilling operations. The environmental inspections focus primarily
on the surface use portion of the approved APD. This includes
inspection of the access road, the well pad, and any pits. While the
BLM does not have the budget or personnel available to inspect every
drilling operation as it is occurring on Federal and Indian minerals,
the BLM conducts inspections in accordance with an annual strategy to
ensure compliance with the regulations, lease stipulations, COAs for
the plan, and permits.
As described above, the BLM has numerous processes and requirements
to ensure that operators conduct oil and gas exploration and
development in an environmentally responsible manner that protects
mineral and other resources.
Within 30 days after the operator completes a well, the operator is
required by Section IV(e) of Onshore Order 1 to submit to the BLM a
Well Completion or Recompletion Report and Log (Form 3160-4), which
provides drilling and completion information. This includes the actual
casing setting depths and the amount of cement the operator used in the
well along with information regarding the completion interval, such as
the top and bottom of the formation, the perforated interval, and the
number and size of perforation holes. The operator is required to
submit copies of all electric and mechanical logs, including any cement
evaluation logs, which the operator ran on the well prior to conducting
completion operations. The BLM reviews this information to ensure that
the operator set the casing and pumped the cement according to the
approved permit.
Once a well goes into production, water is often produced with the
oil and gas. The produced water tends to be of poor quality and is not
generally suitable for drinking, livestock, or other uses without
treatment and, therefore, must be disposed of properly. Onshore Oil and
Gas Order 7 (Order 7) regulates the disposal of produced water. Under
Onshore Order 7, operators must apply to the BLM for authorization to
dispose of produced water by injecting the water into a suitable
formation, by storing it in pits, or by other methods approved by the
BLM. If the disposal is into injection wells, the operator must obtain
approval under the Safe Drinking Water Act's Underground Injection
Control (UIC) program that is administered by the Environmental
Protection Agency (EPA). In many states, the EPA has granted primary
enforcement authority for the UIC program to the state agency
responsible for oil and gas development. If the water will be stored in
pits, the BLM requires specific design standards to ensure the water
does not contaminate the environment or pose a threat to public health
and safety.
After a well has been drilled and completed, the BLM continues to
inspect the well until it has been plugged and abandoned and the
surface has been rehabilitated. During the production phase of the
well, the BLM inspections focus on two primary issues: Production and
the environment. The Federal Government (for Federal leases) or an
Indian tribe or individual Indian allottee (for Indian leases) receives
a royalty on the oil and gas removed or sold from the lease based on
the volume, quality, and value of the oil and gas. Royalties from
Federal leases are shared with the state as provided by statute.
Production inspections are done to ensure the volume and quality of the
oil and gas is accurately measured and properly reported. Environmental
inspections are done to ensure that well pads and facilities are in
compliance with regulations, Onshore Orders, and approved permits.
Environmental inspections include ensuring that pits are properly
constructed, maintained, and protected from wildlife; identifying
leaking wells or pipelines; ensuring that the wellsite and facilities
are properly maintained; and ensuring that proper erosion controls and
rehabilitation measures are in place.
When a well has reached the end of its economic life, Federal
regulations require it to be plugged and abandoned to prevent oil and
gas from leaking to the surface or contaminating water bearing zones or
other mineral zones. 43 CFR 3162.3-4. Well abandonment can be requested
by the operator or required by the BLM. In either case, the operator
must submit a proposal for well plugging, including the length,
location, type of cement, and placement method to be used for each
plug. Onshore Order 2 contains minimum requirements for well plugging.
The operator must also submit a plan to rehabilitate the surface once
the well has been plugged. The goal of surface rehabilitation is to
remove obvious visual evidence of the pad and to promote the long-term
stability of the site and vegetation.
[[Page 61931]]
The BLM inspects both well plugging and surface restoration. Well
plugging inspections are done to ensure the plugs are set into the
wellbore as approved by the BLM. The inspector will witness the depth
and volume of cement used in each plug as well as the physical
verification of the top of each plug. When an operator has complete
surface restoration, it will notify the BLM. The BLM will send surface
protection specialists to ensure the restoration is adequate. Once the
BLM is satisfied with the restoration efforts, the BLM will approve the
operator's Final Abandonment Notice.
II. Discussion of the Final Rule and Comments on the Proposed Rule
On July 25, 2017, the BLM proposed to rescind the 2015 final rule
because we believed that rule was unnecessarily duplicative of state
and some tribal regulations and imposed burdensome reporting
requirements and other unjustified costs on the oil and gas industry.
The 60-day comment period for that proposed rule (the 2017 proposed
rule) ended on September 25, 2017 (82 FR 34464).
Discussion of Comments by Topic
Water Quality
Many commenters state that the 2017 proposal, if finalized, will
have negative impacts on water quality and public health. Commenters
state that science has shown that hydraulic fracturing can be injurious
to the natural landscape as well as to human health and safety.
Commenters state that one danger from hydraulic fracturing is
contamination of surface water by toxic chemicals that leach off site.
Another is that the fluids may leak from the well into underground
aquifers. Commenters assert that contamination on Federal and tribal
land runs off Federal lands into the water systems that we use and
seeps into the groundwater we drink.
The BLM has reviewed incident reports from Federal and Indian wells
since December 2014. This review indicated that resource damage is
unlikely to increase by rescinding the 2015 rule because of the rarity
of adverse environmental impacts that occurred from hydraulic
fracturing operations before the 2015 rule, and after its promulgation
while the 2015 rule was not in effect. The BLM believes that the
appropriate framework for mitigating these impacts is through the state
regulations, through tribal exercise of sovereignty, and through BLM's
own pre-existing regulations and authorities (pre-2015 final rule 43
CFR subpart 3162 and Onshore Orders 1, 2, and 7). The review and
approval of the APDs requires compliance with those existing
authorities and regulations to ensure protection of the water
resources, and the local environment.
Multiple commenters claim that hydraulic fracturing is a dangerous
practice that can contaminate our air and water, while contributing to
the release of greenhouse gases. One commenter states that, as the base
of scientific knowledge regarding risks from hydraulic fracturing
continues to develop, the evidence continues to build that hydraulic
fracturing and shale and tight gas development processes pose a wide
range of risks to human health and the environment. Another commenter
asserts that no amount of regulation can make hydraulic fracturing
safe, but that rescinding or weakening the recently updated rules only
puts our shared resources at greater risk. Further, the commenter
states that the updated rules are long overdue and simply lay out basic
standards to follow. Commenters state that the 2015 rule was enacted
after years of review and should not be weakened or repealed.
Commenters state that rescinding the 2015 rule would put our Federal
lands at risk by repealing our first line of defense against
groundwater contamination.
The BLM initiated the development of the hydraulic fracturing rule
in 2010 in response to public concerns. Relatively few states had any
regulations on hydraulic fracturing at that time. In light of this, a
BLM regulation covering wellbore integrity and usable water protection
seemed appropriate at that time. Since promulgation of the 2015 rule,
however, many states have updated their regulations to address
hydraulic fracturing operations. The BLM now believes that the 2015
rule is duplicative of the states' and some tribal regulations, as well
as some of the BLM's own pre-existing regulations and authorities (pre-
2015 rule 43 CFR subpart 3162 and Onshore Orders 1, 2, and 7), and is
not necessary.
Some commenters are concerned that hydraulic fracturing affects the
availability of water resources. These commenters describe that once
water is used for hydraulic fracturing, it cannot be returned to the
water table and that water is a precious resource that should not be
depleted in this fashion.
Recycling and reuse of flowback fluids from ongoing hydraulic
fracturing operations is currently practiced in many states, but the
majority of recovered fluids are still injected into disposal wells
regulated under the Safe Drinking Water Act (SDWA). The 2015 rule,
however, would not have mandated reuse or recycling. Therefore,
rescinding the 2015 rule will not affect demands on water supplies or
the reuse or recycling of recovered fluids.
One commenter states that, although incidents of contamination of
groundwater from hydraulic fracturing are not frequent, due in part to
improvements in technology, they have occurred in locations that raise
concern about the adequacy of protection. In response to comments that
list examples of studies that find no linkages between hydraulic
fracturing and groundwater contamination, one comment points to the
work of a former U.S. EPA scientist linking hydraulic fracturing with
groundwater contamination. The commenter adds that not all laboratory
tests have shown contamination of groundwater in areas of hydraulic
fracturing because standard laboratory tests do not always test for
exotic, highly water-soluble chemicals used in hydraulic fracturing.
The referenced study suggested that water wells in Pavillion, WY
were contaminated with hydraulic fracturing wastes that had been stored
in unlined pits dug into the ground. The BLM has several existing
requirements, some of which are set out at 43 CFR subpart 3162 and in
Onshore Oil and Gas Orders 1, 2, and 7, that allow it to mitigate the
risks associated with oil and gas operations, including any risks to
groundwater from hydraulic fracturing operations. The BLM also
possesses discretionary authority allowing it to impose site-specific
protective measures reducing the risks associated with hydraulic
fracturing. The BLM Authorized Officers follow the BLM's regulations
and authorities to review and approve each APD. Operators also must
comply with existing state laws and regulations and, on tribal lands,
tribal laws and regulations, including those that are intended to
prevent groundwater contamination. The BLM does not believe that the
2015 final rule would reduce the risks of groundwater contamination to
an extent that would justify the burdens imposed on operators or the
BLM by that rule.
One commenter states that the cost of cleaning groundwater after it
is contaminated is exorbitant and therefore that circumstances
potentially causing contamination should be avoided.
We agree. The BLM Authorized Officers follow the BLM's regulations
and authorities (pre-2015 rule 43 CFR subpart 3162 and Onshore Orders
1, 2, and 7) to review and approve each APD. Operators also must comply
with existing state regulations, or, on tribal lands, tribal laws.
Those requirements are intended to ensure protection of the
[[Page 61932]]
water resources and prevent any groundwater contamination. We are no
longer persuaded, though, that the 2015 rule would improve protection
of groundwater to an extent that would justify the burdens on operators
or the BLM.
One commenter takes issue with the statements in the 2017 proposed
rule that, ``a review of incident reports from Federal and Indian wells
since December 2014,'' indicates that, ``resource damage is unlikely to
increase by rescinding the 2015 final rule.'' The commenter asserts
that the BLM provides no support or explanation for this statement and
has failed to consider many of the significant adverse environmental
impacts associated with rescinding the 2015 rule.
The BLM did not find any increase in the number of incidents
related to hydraulic fracturing completions in BLM operations since
December 2014. The EPA study (EPA 2016) on hydraulic fracturing was
unable to identify any specific activities of hydraulic fracturing
operations on Federal or Indian lands that impacted the drinking water
resources, because the study did not distinguish between hydraulic
fracturing on Federal or Indian lands and hydraulic fracturing on other
lands.
One commenter states that he has lived in North Dakota for five
years and personally witnessed the purposeful dumping of hydraulic
fracturing water along roads and ditches on the roads leading to
hydraulic fracturing sites. The commenter states that most of the oil
and hydraulic fracturing waste spills that happen on or near sites do
not get reported.
The 2015 rule did not address open dumping of recovered fluids.
Neither the 2015 rule, nor this rule, alter the requirement that
permanent disposal of produced water must be in accordance with an
approved plan. See Onshore Oil and Gas Order No. 7, 58 FR 47354 (1993).
Unpermitted dumping of recovered fluids is outside the scope of this
rulemaking.
Multiple commenters assert that BLM's rescission of the 2015 rule
is appropriate because there has been no proven case of groundwater
contamination from hydraulic fracturing in the United States to date.
Several commenters state that studies developed by the EPA and U.S.
Geological Survey (USGS) indicate that hydraulic fracturing has not had
an impact on groundwater quality. One commenter further states that
several studies, including an EPA study, a Yale University study, and a
study funded by the Natural Resources Defense Council, find no
incidence of contamination of groundwater due to hydraulic fracturing,
which has been performed on over 1.2 million wells since 1948. Absent
any confirmed instances of hydraulic fracturing impacting underground
sources of drinking water, a commenter asserts that there is no
protective advantage to the environment from the 2015 rule.
The BLM generally agrees with the commenter. We conclude that state
and some tribal regulations, in conjunction with the BLM's own pre-
existing regulations and authorities (pre-2015 rule 43 CFR subpart 3162
and Onshore Orders 1, 2, and 7) have been effective in ensuring
protection of the water resources and the local environment.
One commenter states that any studies contained in the BLM's
original administrative record that suggest that a link exists between
groundwater contamination and oil and gas production were focused on
well construction rather than hydraulic fracturing as the cause of the
contamination. The commenter further states the BLM and each of the
states in which Federal oil and gas is produced had well construction
rules prior to the 2015 rule, and that the BLM's administrative record
does not provide any evidence that a rule focused on hydraulic
fracturing would improve the degree of protection related to well
construction.
The BLM agrees in part. Onshore Oil and Gas Order No. 2 continues
to apply to the drilling and cementing of oil and gas wells on Federal
and Indian lands. See 53 FR 46798 (1988). The 2015 rule would have
imposed additional monitoring, testing, and reporting requirements. In
the preamble and supporting documents for the 2015 rule, though, the
BLM cited a few instances where surface or groundwater contamination
was caused by inter-well communications during the hydraulic fracturing
operations. Those were not directly linked to wellbore construction,
but rather caused by geologic fractures and fissures which are
prevalent in some areas, or by lack of awareness of other wellbores.
However, the BLM also possesses discretionary authority allowing it to
impose site-specific protective measures that can be applied when
necessary to reduce the risks associated with hydraulic fracturing.
One commenter noted that, in Federal court, an oil company was
found to have caused permanent and irreparable pollution of the Sac and
Fox Nation's groundwater by oil and gas activities. As a result of
ineffective and absent regulatory actions, portions of the Sac and Fox
Nation's aquifer will be unsafe to drink for generations.
It appears that the operator in the cited case did not follow the
conditions of the permit issued by the BLM for the operation, and is
responsible for the damage. The BLM's 2015 rule would not have
addressed such issues related to violation of the rule on tribal lands
and neither would this rule.
One commenter describes that the 2015 rule would have redefined
``usable water,'' modifying the term's definition to include ``those
waters containing up to 10,000 parts per million (ppm) of total
dissolved solids.'' The commenter asserts a lack of any empirical
evidence or science-based support for a need to protect water that is
so saline that it can kill livestock, and asserts that this definition
would expand the scope of protected waters well beyond EPA's
regulations under the Safe Drinking Water Act.
Onshore Oil and Gas Order No. 2, Section II. Y, states that
``Usable Water means generally those waters containing up to 10,000 ppm
of total dissolved solids.'' The BLM believes that the standard set
forth in Onshore Order No. 2 is appropriate and it will continue to
follow that standard.
Air Quality/Public Health
One commenter states that there are unsafe levels of air pollution
at every stage of oil and gas development. Air quality testing at
hydraulic fracturing sites in several states have revealed levels of
hydrogen sulfide and volatile organic compounds capable of causing
respiratory, neurologic, and cardiovascular disease, blood dyscrasias,
birth defects, and malignancies after chronic and recurrent exposure.
The commenter claims that we do not yet know the true level of risk
related to air contamination for workers, neighboring families and
communities. The commenter asserts that flowback, even when stored in
closed tanks, can liberate toxic volatile pollutants (such as
carcinogenic benzene) at very high concentrations into the atmosphere.
The commenter states that workers should be wearing respirator masks to
minimize serious health consequences.
In response to that comment, the BLM notes that the 2015 rule would
have generally required recovered fluids to be stored in tanks until a
permanent disposal plan was approved, but allowed for exceptions and
did not require closed or vapor-recovery systems. The 2015 rule was
never intended to be an air quality or emissions regulation. Health
effects from air emissions and mitigation measures were not addressed
in the 2015 rule and are outside the scope of this rule. Air quality
and worker safety
[[Page 61933]]
are regulated by other Federal, state, or tribal agencies.
One commenter states that a new form of hydraulic fracturing-
related air pollution may be increased levels of indoor radon
concentration (the number one cause of lung cancer among non-smokers)
in homes located in areas where hydraulic fracturing is used to extract
natural gas from shale formations. The commenter highlights that a
peer-reviewed study published in May 2015 by the National Institute of
Environmental Health Sciences, ``Predictors of Indoor Radon
Concentrations in Pennsylvania, 1989-2013,'' documents a progressive
upward trend in ambient radon levels between 2005 and 2013 coincident
with the onset of hydraulic fracturing in Pennsylvania. The commenter
noted that, at present, there are no state or Federal regulations
addressing this newly discovered association.
In response to that comment, the BLM notes that the 2015 rule did
not address radon concentrations, and rescinding that rule will not
affect radon concentrations. Radon ``association'' with hydraulic
fracturing operations is outside the scope of this rulemaking.
One commenter states that unsafe levels of air pollution found near
hydraulic fracturing sites are largely ignored by Federal and state
agencies. The commenter suggest that, to remedy this, monitoring of
pollution emissions, air testing of communities, and strict standards
to limit pollution are sorely needed and should replace patchy,
inadequate state protections that do not do enough to safeguard
communities that are increasingly exposed to the deadly consequences of
poorly regulated hydraulic fracturing sprawl. Another commenter states
that diesel emissions from heavy trucks and machinery used during well
site preparation, drilling, and production contain toxins and release
diesel soot particles, which increase health risks including: Asthma
attacks, cardiopulmonary disease, respiratory disease, pregnancy
complications, and premature death. In addition, the commenter states
that inhaling respirable silica can cause silicosis and lung cancer in
miners, sandblasters, and foundry workers. The commenter further notes
that, due in large part to methane leakage and venting, the greenhouse
gas footprint of shale gas is larger than the footprint of oil,
conventional gas, and even coal.
These comments are outside the scope of the present rulemaking
action. Neither the 2015 rule nor this rescission will cause air
pollution, fugitive dust, or greenhouse gas emissions to be greater or
less. Air quality monitoring and emissions standards are regulated by
other agencies.
In addition to air and water pollution, one commenter expressed
concern about externalities of drilling operations, such as noise
pollution and odors, which should be kept within tolerance levels as
drilling expands to areas where more people live.
This comment is outside the scope of this rulemaking because it
addresses oil and gas development in general and fails to assert any
specific alternative approach or change from the 2017 proposed rule
that the BLM should have considered in this final rule with respect to
the regulation of hydraulic fracturing operations on Federal and Indian
lands.
Chemical Disclosure
In this section, we describe the comments the BLM received
regarding chemical disclosure and respond to them all in the final
paragraph of the section.
Some commenters are concerned that rescinding the 2015 rule will
result in chemicals used in the hydraulic fracturing process not being
disclosed by operators. Commenters state that, as the Federal lands
managed by the BLM are public lands, the public has a right to clearly
understand what is occurring on them and any potential impacts that
those activities could have on water resources. One commenter notes
that a recent study conducted by the Yale School of Public Health found
that, of the compounds used in hydraulic fracturing that they could
identify and study, 44 percent of the water pollutants and 60 percent
of air pollutants were either confirmed or possible carcinogens.
Although these compounds often make up only a small percentage of the
total volume of the fluid, many are known to be toxic to humans at
levels as low as five parts per billion. The commenter suggests that
the 2015 rule would help to ensure proper handling and would mitigate
potential exposure and impacts to public health from hydraulic
fracturing. Another commenter describes a 2015 report published by the
EPA that stated that well operators refused to disclose 11 percent of
their ingredient records, citing them as confidential business
information. Furthermore, one or more ingredients in more than 70
percent of disclosures were omitted, according to the commenter.
One comment referred to a 2016 article entitled, ``Hydraulic
Fracturing Chemicals Reporting: Analysis of Available Data and
recommendations for Policy Makers,'' which highlighted that 16.5
percent of chemicals used in hydraulic fracturing between the years
2012 and 2015 were unreported.
One commenter expressed concern regarding the BLM's reliance on a
third party (FracFocus) to replace specific transparency and public
accountability. In response to commenters on the 2015 rule, the BLM
stated that, ``compliance with these rules will increase transparency
of the hydraulic fracturing approval process and provide a means for
disclosure to the public of the fluids utilized in the hydraulic
fracturing process.'' The commenter complains that the BLM now states
that disclosure of the chemical content of hydraulic fracturing fluids
to states or databases, such as FracFocus, is more prevalent than it
was in 2015 and so there is no need for a Federal chemical disclosure
requirement. The commenter asserts that the slight shift in reporting
frameworks is insufficient justification to remove regulations that
promote administrative transparency and public disclosure of
potentially harmful chemicals. Furthermore, the commenter stated that
the BLM has yet to respond to questions from the Secretary of Energy's
Advisory Board raised in 2015 with respect to technical issues with
FracFocus, including a lack of verification for data accuracy.
One commenter states that the BLM's analysis of state requirements
for chemical disclosure indicates that all states reviewed require
chemical disclosure of hydraulic fracturing fluids to FracFocus (with
the possible exception of New Mexico). The commenter states that the
BLM rule, however, requires much more than just disclosure of chemicals
used in the fracturing fluid. The commenter asserts that California is
the only state that has equivalent requirements for each of the
elements that had been required in the 2015 rule and the only other
state that has any equivalent requirements is Wyoming.
One commenter states that radioactive substances are used in
hydraulic fracturing fluid to determine the injection profile and
location of fractures created by hydraulic fracturing. The commenter
asserts that these chemicals should be heavily regulated as a matter of
national security and that all chemicals onsite should be identified
and reported by the operator. The commenter states that the contents of
all materials and quantities injected into the wells should be
documented, reported, and provided upon request. The commenter states
that polluters should not remain unidentified because the identifying
features of the injected slurry are protected as ``trade secrets.''
[[Page 61934]]
Some commenters assert that it is not burdensome to require the oil
and gas industry to disclose the chemicals they are pumping into the
ground in order to extract petroleum.
In response to all of the foregoing comments in this section,
although we agree that the information is readily available to the
operators or their contractors, we are no longer convinced that a BLM
regulatory requirement would improve access to that information
sufficiently to justify the cost of compliance.
Most states with existing oil and gas operations now have
regulations that require operators to disclose the chemical content of
hydraulic fracturing fluids to either a publicly accessible forum, such
as FracFocus, state regulatory agencies, or both. This includes the
States of California, Colorado, Montana, New Mexico, North Dakota,
Oklahoma, Texas, Utah, and Wyoming, which accounted for approximately
99 percent of the total well completions on Federal and Indian lands
from fiscal year (FY) 2010 to 2016. In addition, there are 25 states
that currently use FracFocus for chemical disclosures. These include
seven states, Colorado, Montana, New Mexico, North Dakota, Oklahoma,
Texas, and Utah, with substantial BLM administered oil and gas
operations. The BLM now believes that the disclosures of the chemical
content of hydraulic fracturing fluids to state regulatory agencies
and/or databases, such as FracFocus is more prevalent than it was in
2015 and that there is no need for a duplicate Federal chemical
disclosure requirement, since companies are already making those
disclosures on most of the operations, either to comply with state law
or voluntarily. Furthermore, the 2015 rule did not require disclosure
of trade secrets. See generally, 18 U.S.C. 1905; 43 CFR 3162.3-3(j)
(2016). Therefore, there is no reason to believe that rescinding the
2015 rule will cause operators to withhold more confidential
information about chemicals used in hydraulic fracturing operations. To
the extent that the comments address control of hazardous substances
generally, they are beyond the scope of this rulemaking.
Earthquakes
Some commenters suggest that there is a link between earthquakes
and hydraulic fracturing of rock formations. One commenter states that
significant seismic activity is allowed without any state or Federal
constraints. Commenters suggest a link between hydraulic fracturing and
wastewater injection and earthquakes in Oklahoma and Ohio. Several
commenters describe a 2016 study that cautioned that hydraulic
fracturing in the United States may be causing higher-than-recognized
induced earthquake activity that is being masked by more abundant
wastewater-induced earthquakes. The commenters assert that the
injection of oil and gas wastewater, often associated with hydraulic
fracturing, has been linked to the dangerous proliferation of
earthquakes, including damaging earthquakes in many parts of the
country.
In addition, one commenter asserts that the hydraulic fracturing
industry has burdened tribal businesses and homeowners that have to pay
to repair damages inflicted by these earthquakes. The commenter asserts
that induced seismicity prevents tribal members from access to
Department of Housing and Urban Development (HUD) funds for home
construction in areas that are now unable to be adequately insured for
earthquake damage.
In response to the comments, U.S. Geological Survey research
indicates that most induced seismicity has been linked to wastewater
injection, and seldom to hydraulic fracturing operations. While the
2015 rule contains provisions regarding the storage of recovered
fluids, it did not include any provisions regarding wastewater disposal
by underground injection, which is regulated under the SDWA by the EPA
or an approved state or tribe. The 2015 rule also did not change the
provisions of 43 CFR 3162.3-2 that apply to injection activities.
Pursuant to Onshore Order 7, operators must submit a wastewater
disposal plan prior to commencing operations, and they must provide the
BLM with a permit from the EPA, state or tribe along with this plan.
Even if hydraulic fracturing operations were found to cause damaging
seismicity, the 2015 rule would not have controlled the effect, and,
therefore, rescinding that rule will not increase the likelihood of
seismicity damage.
Rule Authorities
Commenters expressed a variety of opinions about whether the BLM
has statutory authority to regulate hydraulic fracturing operations on
Federal and Indian lands. This section of the preamble first summarizes
the arguments for the BLM's statutory authority (and duty) and responds
to them. It next summarizes the arguments against the BLM's authority
and responds to them.
Some commenters assert that the BLM has clear authority to regulate
hydraulic fracturing while other commenters disagree. More
specifically, some commenters state that the BLM issued the 2015 rule
as part of carrying out its statutory duties to prevent unnecessary or
undue degradation of public lands consistent with 43 U.S.C. 1732(b) and
to issue ``comprehensive'' regulations ``necessary to implement the
provisions'' of FLPMA, and to ``carry out the purposes of [FLPMA] and
of other laws applicable to the public lands.'' In addition, the
commenters state that, under the MLA, Congress charged the BLM with
ensuring that Federal lessees conduct their operations with
``reasonable diligence, skill and care,'' and instructed the BLM to
protect the ``interests of the United States'' and ``the public
welfare.'' The commenters state that Congress authorized the BLM to
``prescribe necessary and proper rules and regulations and to do any
and all things necessary to carry out and accomplish the purposes'' of
the MLA. These commenters conclude that the 2015 rule is consistent
with the BLM's duties under FLPMA and MLA.
Similarly, some commenters state that BLM lands are multiple use
lands that must fulfill not only resource acquisition goals but public
recreation and public benefit goals. The commenters state that actions
must be consistent with all the uses of BLM property and the BLM cannot
make this determination without the information requested in the 2015
rule. Some commenters assert that activity on public lands must be
regulated consistently across the nation, especially when activities
may affect the ability of the BLM to uphold its multiple use mandate.
Some commenters argue that the proposed action indicates a preference
for oil and gas leasing and development over other multiple uses. The
commenters argue that this mandate prohibits DOI from managing public
lands primarily for energy development or in a manner that unduly or
unnecessarily degrades other uses.
Some commenters state that the proposed rescission rule is
inconsistent with the BLM's statutory duties under FLPMA, the MLA, and
the IMLA. The commenters state that the BLM concluded in 2015 that the
requirements of the 2015 rule were necessary to meet those obligations.
The commenters assert that the BLM's proposed reversal of the 2015 rule
is not permissible under FLPMA and other laws because the BLM failed to
explain its departures from the factual conclusions it drew when
promulgating the rule in 2015.
Similarly, some commenters state that it is a dereliction of duty
to abdicate the responsibility of management of the
[[Page 61935]]
appropriate and proper use of public lands to the states. Commenters
state that they rely on BLM oversight to manage the use of these public
lands for the benefit of all Americans, not just the profits of oil and
natural gas companies. Commenters assert that the 2017 proposed rule,
if finalized, is guided by the short term interests of a few at the
expense of long-term efforts to protect our lands and most importantly,
our water.
We agree in part with the comments in the previous four paragraphs.
The BLM's actions related to oil and gas operations on Federal land are
subject to FLPMA, MLA, the Mineral Leasing Act for Acquired Lands
(MLAAL), and other statutes. FLPMA prescribes that the public lands are
to be managed for multiple use and sustained yield, and that the BLM is
to prevent unnecessary or undue degradation. The MLA requires that
Federal oil and gas leases include provisions to ensure the exercise of
reasonable diligence, skill, and care in operations. No court, however,
has held that FLPMA requires BLM to manage each acre of public land to
support all uses at all times. Rather, oil and gas operations are
statutorily authorized uses of the Federal lands, and thus may be
thought of as ``necessary or due'' degradation when conducted according
to appropriate standards for protection of the lands and associated
resources.
With respect to legal duties, no statute requires the BLM to
regulate hydraulic fracturing operations, and no statute requires all
oil and gas operations on Federal lands to be subject to the same
regulations. (Indeed, lease stipulations and COAs are often different
in different areas to address local conditions.) Rather, the contents
of operating regulations are within the discretion of the Secretary.
Mineral Policy Ctr. v. Norton, 292 F. Supp. 2d 30, 44-45 (D.D.C. 2003).
State laws have always applied to oil and gas operations on public
lands, even when those laws differ from one another. Particularly
where, as here, there is no compelling indication that modern state
regulations are allowing unnecessary or undue degradation to the public
lands, the Secretary is within his discretion to decide that rescinding
the 2015 rule would reduce the burdens both on operators and the BLM,
with little reduction in the protection of those lands.
This final rule represents no dereliction of duty. See generally,
Gardner v. BLM, 638 F.3d 1217, 1222 (9th Cir. 2011). Furthermore, it
has nothing to do with decisions about which Federal lands to open for
leasing, or which parcels to be offered for lease. Private, for-profit,
development of oil and gas on Federal lands is authorized by the MLA,
the MLAAL, and other statutes, and thus objections to those
authorizations are outside the scope of this rulemaking.
Other commenters assert that the BLM lacked authority to issue the
2015 rule. Some commenters argue that Congress has not delegated
authority to the BLM to regulate hydraulic fracturing and has granted
only limited authority to the EPA to regulate hydraulic fracturing
under the Safe Drinking Water Act (SDWA). Another commenter states that
the BLM concedes that it cannot regulate enhanced oil recovery,
disposal wells, or hydraulic fracturing using diesel because Congress
has designated the EPA as the agency with regulatory authority over
those forms of underground injection in the SDWA, and the same
conclusion should apply with respect to non-diesel hydraulic
fracturing.
Some commenters argue that the 2015 final rule requirement to
submit water source and recovered fluid disposal method encroaches upon
state jurisdiction over waters of the state and over underground
injection control covered in the primacy agreement between North Dakota
and the EPA in 1983.
A commenter asserts that North Dakota has a large number of
``split-estate'' tracts where the Federal minerals have been severed
from the surface estate, which is owned by either the State of North
Dakota or private parties. The commenter argues that the 2015 final
rule inappropriately broadened BLM's authority to regulate surface
operations for hydraulically fractured wells that penetrate Federal
minerals, but where the United States does not own the surface.
With few exceptions, the arguments described in the previous three
paragraphs were raised in the litigation challenging the 2015 rule. We
believe that rescinding the 2015 rule alleviates these concerns and,
therefore, the BLM need not address them here. The more immediate point
is that the BLM has authority to rescind the 2015 rule, and to restore
the regulations existing prior to the 2015 rule with the few exceptions
previously discussed. Those regulations were promulgated in 1982 and
amended in 1988. See 43 CFR 3612.3-2 (2014); 47 FR 47765 (1982); 48 FR
36583 (1983); 52 FR 5391 (1987); 53 FR 17363 (1988); 53 FR 22847
(1988). No commenter provided evidence that this rescission would
interfere with the regulation of underground injections by states,
tribes, or the EPA under the SDWA (as amended). The BLM does not
regulate disposal wells; but BLM's authorization is required for use of
BLM-managed surface for a disposal well. Other ``enhanced recovery''
operations are also outside the scope of this rulemaking. Aside from
``split estates'' being common in several states where the BLM
regulates oil and gas operations, no commenter provided evidence that
rescission of the 2015 rule would be ``inappropriate'' as applied to
split-estate lands. If after this rescission of the 2015 rule, the BLM
needs to approve an operation that would, for example, require
substantial quantities of water, the requirements of NEPA and the
applicable regulations would apply.
One commenter states that, regardless of the 2015 rule, the BLM
already has the ability to impose additional conditions related to
hydraulic fracturing on operators. This includes the authority to
require the submission of additional information in relation to the
permitting process as well as the ability to require that specific
actions be taken by operators on-site to minimize environmental impacts
and ensure site safety and security. The commenter states that the
agency has broad authority to collect information. The commenter also
noted that, pursuant to 43 CFR 3160.0-9, the BLM may request data so
that proposed operations may be approved or to enable the monitoring of
compliance with granted approvals, and operators must respond to such
requests as a condition of Federal oil and gas leases and as a
precondition to issuance of a permit to drill. Finally, the commenter
notes that the BLM also has the authority to require operators to take
specific actions when developing a lease.
The commenter is essentially correct. After this rescission, the
BLM will continue to responsibly use its authorities to carry out its
duties under the applicable statutes and regulations.
One commenter criticizes the BLM's intention to restore the
regulations under which prior approval is required for ``non-routine''
hydraulic fracturing operations. 43 CFR. 3162.3-2 (2014). The commenter
asserts that the BLM has never treated the ``fracturing'' referred to
in 43 CFR. 3162.3-2 as equivalent to hydraulic fracturing. The
commenter further argues that proponents of the 2015 rule have
recognized that under 43 CFR. 3162.3-2 ``companies generally treated
all hydraulic fracturing operations as routine'' and the BLM did not
exercise approval authority over hydraulic fracturing.
In response to this and other similar comments, the BLM
reconsidered its proposal to restore the regulatory text in
[[Page 61936]]
43 CFR 3162.3-2(a) (2014) requiring prior approval for ``nonroutine
fracturing jobs.'' As a result of this review, the BLM decided not to
restore the ``nonroutine fracturing'' requirement in this final rule.
As previously mentioned, prior to the 2015 rule, the regulations at
43 CFR 3162.3-2(a) (2014) provided in pertinent part that a ``proposal
for further well operations shall be submitted by the operator on Form
3160-5 for approval by the authorized officer prior to commencing
operations to . . . perform nonroutine fracturing jobs. . . .'' Those
regulations, however, did not define ``nonroutine fracturing jobs'' or
provide guidance to operators or the BLM authorized officers on how to
distinguish ``routine'' from ``nonroutine.''
The BLM further notes that as a result of considerable advances in
oil and gas development technology in the last 20 years, hydraulic
fracturing practices that would have been considered ``nonroutine''
when the BLM originally issued the regulations requiring prior approval
for ``nonroutine fracturing jobs'' are now commonly employed and
considered ``routine.'' The combination of advances in oil and gas
development technology and the BLM's existing authority to mitigate the
potential risks of hydraulic fracturing operations through site-
specific protective measures that are applied as a part of the
environmental review and approval process at the APD stage has made
post-APD approvals for ``nonroutine fracturing jobs'' at most a very
rare occurrence. In fact, while the BLM has not been tracking requests
for approval of ``nonroutine fracturing jobs,'' recent inquiries to BLM
state offices have not revealed any examples of ``nonroutine
fracturing'' requests or approvals. Thus, given that the ``nonroutine
fracturing'' requirement has not, and will not foreseeably serve any
purpose, and that removing it from the regulations could reduce the
potential for unproductive confusion or paperwork without adverse
effects, the BLM has removed ``nonroutine fracturing'' from 43 CFR
3162.3-2(a) in this final rule.
As for whether the word ``fracturing'' in 43 CFR 3162.3-2 (2014),
includes hydraulic fracturing, both the plain meaning and its use in
the industry, includes ``hydraulic fracturing.'' See, e.g., Williams &
Myers Manual of Oil and Gas Terms, p. 420 (10th ed. 1997) (quoting
American Gas Ass'n, Glossary for the Gas Industry (3d ed. 1981)). The
BLM has always interpreted that regulation to include hydraulic
fracturing. The commenter does not offer any other rational
interpretation. Therefore, including ``routine fracturing'' in the
restored section 3162.3-2(b) makes plain that an operator does not need
the BLM's prior approval for hydraulic fracturing operations, except
those that involve increased surface disturbance or that do not conform
to the standard of prudent operating practice.
Adequacy of Existing Regulations and Industry Practices
The following paragraphs summarize comments regarding whether
existing regulations and industry practices are adequate to protect
public lands. We first summarize and respond to comments critical of
the existing regulations and industry practices, and opposed to
rescission of the 2015 rule. Then we summarize and respond to comments
arguing that existing state and Federal regulations and industry
practices provide adequate protection for federal lands and associated
resources, and in favor of rescission of the 2015 rule.
Multiple commenters state that when the BLM rescinds the 2015 rule,
regulations would be as they existed prior to adoption of the 2015
rule. One commenter states that it is apparent that almost no oversight
of hydraulic fracturing was required prior to the 2015 rule, however,
and that the inadequacy of the prior regulation for dealing with issues
related to hydraulic fracturing was noted in the rulemaking process for
the development of the 2015 rule. The commenter states that the prior
regulations required that the BLM approve proposals for ``further well
operations,'' which included ``nonroutine fracturing jobs'' and eight
other activities. The commenter states that no BLM approval was
required for ``routine fracturing'' jobs unless there was additional
surface disturbance. However, the commenter states that ``nonroutine
fracturing jobs'' was not a defined term and the BLM proposes to
continue to not define the term. The commenter states that the lack of
defined distinction between nonroutine hydraulic fracturing jobs and
routine hydraulic fracturing jobs made ``this distinction functionally
difficult to apply and confusing for both the agency and those
attempting to comply with the regulations.'' The commenter states that
the BLM therefore acknowledges that almost all fracturing operations
were deemed routine and not requiring approval from the BLM prior to
commencing operations. A separate commenter notes that this ``pre-
existing authority'' clearly existed at the time the 2015 rule was
promulgated and fails to provide a valid basis for the BLM's change in
position.
Multiple commenters express concern that state laws are
insufficient to regulate hydraulic fracturing activities. The
commenters state that, while some states have requirements regarding
particular issues that are equivalent to the 2015 rule, many gaps in
regulation remain. The commenters state that each state has areas where
its regulations are weaker than the 2015 rule, and no state requires
the same best practices across the board. The BLM should keep the 2015
rule in place to ensure consistent protections across the dozens of
states with existing Federal oil and gas leases. One commenter notes
that, if the BLM recognizes that certain states have less comprehensive
regulations and enforcement mechanisms, it necessarily concedes that
the legal framework within those states will not provide the same
protections as the regulations promulgated by the 2015 rule and
therefore that the 2015 rule is not duplicative of state regulations.
Another commenter offers that the 2015 rule provided specific direction
to states on how to protect groundwater and other resources and set
forth a common standard of environmental protection at hydraulic
fracturing sites and brought together requirements for a set of
environmentally protective requirements that could be easily referenced
in one place for consistent implementation.
Multiple commenters argue that the BLM's analysis of state
regulations included in the RIA suggests the 2015 rule is not
redundant. In particular, two commenters highlight that the BLM, in its
discussion of the mechanical integrity test requirement, states it ``is
an industry recommended practice and is required by almost all of the
states whose regulations we reviewed.'' One commenter states that the
BLM rule requires operators to perform a successful mechanical
integrity test prior to fracturing at a test pressure equal to that
which will be applied during the actual fracturing operation and that
the applied pressure must hold for 30 minutes with no more than a 10
percent pressure loss. The commenter states that only California and
Montana have rules that include these requirements. The commenter
states that similar issues exist with regard to the annulus pressure
monitoring and reporting provisions. The commenter states further that,
in its analysis of state regulations for monitoring pressure during
hydraulic fracturing operations, the BLM claims that all states
reviewed, other than New Mexico, Oklahoma, and Utah, explicitly require
monitoring
[[Page 61937]]
during fracturing operations. The commenter states that, as with state
mechanical integrity test rules, the mere presence of a rule is not
sufficient. Rather, the commenter states, the substance of state rules
must be analyzed to determine whether state rules contain safeguards
equivalent to the BLM rule. In addition, with respect to review of the
storage tank requirements, some commenters state that the BLM
acknowledges that ``Although the use of tanks is reportedly common,
only 5 out of the 9 states in our in-depth regulatory review had
requirements specifying that operators must use tanks.''
One commenter asserts that the fact that all 32 states currently
with Federal oil and gas leases now have laws or regulations that
address hydraulic fracturing operations in no way indicates those
regulations are sufficient to fulfill the stipulations under Executive
Order 13783, Promoting Energy Independence and Economic Growth. Another
commenter highlighted that despite the existence of state requirements,
the BLM explained in 2015 that ``a major impetus for a separate BLM
rule is that states are not legally required to meet the stewardship
standards that apply to public lands and do not have trust
responsibilities for Indian lands under Federal laws.'' 80 FR 16133;
see id. at 16154. The commenters assert that ``an additional 12 states
have introduced laws or regulations'' regarding hydraulic fracturing is
a natural consequence of the significant public concern about the
practice, but does not obviate the need for Federal regulatory
standards that promote the responsible development of public lands and
fulfill BLM's own independent statutory duties to ensure that oil and
gas operations on Federal and Indian lands are performed in a safe,
responsible, and environmentally protective manner.
One commenter states that, unlike BLM's 2015 rule, many states do
not require operators to obtain a permit specifically for fracturing
operations. The commenter notes that, of the states the BLM reviewed in
the RIA, only California, Montana, and Wyoming require a permit for
fracturing operations. The commenter notes that Oklahoma and Colorado
require notification before fracturing, while New Mexico, North Dakota,
Texas, and Utah require neither a permit nor advanced notification. The
commenter states that this is a significant difference between state
regulations and the 2015 rule.
One commenter specifically claims that New Mexico is second only to
Wyoming in the number of producing oil and natural gas leases on
federally managed land, yet state regulations lack important safeguards
included in the 2015 rule. The commenter notes that, for example, New
Mexico's hydraulic fracturing regulations do not include measures to
prevent ``frack hits,'' which occur when the hydraulic fracturing of
one well causes a pressure transfer that interferes with production in
another well. The commenter states that, as acknowledged in the EA for
the rescission of this rule, these frack hits pose a tangible threat to
water resources and the ecological integrity of public land subjected
to excessive and haphazard drilling.
One commenter contends that the 2015 rule contains two essential
safety components: Wellbore testing prior to hydraulic fracturing and
storage of flowback waste in tanks rather than pits. The commenter
states that these two areas, if not adequately regulated, present
significant risks of environmental contamination. The commenter asserts
that the 2015 rule represented improvements over existing Federal and
Colorado state rules in these areas. The commenter states that, in
proposing to rescind them, the BLM clearly recognized what researchers
have also concluded: Hydraulic fracturing poses pollution risks to air,
soil and water that are highly correlated with failure to ensure
wellbore integrity and pit storage of waste. The commenter states that
the 2015 rule is the BLM's best determination, based on its own
expertise and expert outside input, for preventing such contamination
and the rule should therefore not be rescinded.
One commenter stated that BLM's suggestion that a major expansion
of state regulation has occurred since 2015 is misleading because the
states with new regulations represent an insignificant fraction of
Federal oil and gas development.
One commenter states that the Appendix to the EA for the proposed
rule showed that the new state regulations lack many of the protections
imposed by the 2015 rule. The commenter states that, for example, most
state regulations do not mandate the use of tanks instead of open pits,
do not require measures to prevent frack hits, and do not require the
same measures to ensure adequate cementing.
One commenter said that the BLM assumes substantial continued use
of storage tanks by operators in many states even after the rule is
rescinded, although this is implausible. The commenter states that, for
example, the BLM assumes that 100 percent of operators in Texas and New
Mexico will use tanks even after rescission because of state
regulations despite the fact that both states allow exemptions to their
regulatory standards. The commenter states that the BLM also assumes
100 percent voluntary compliance in Utah despite the state's
``unclear'' standards, and 92 percent voluntary compliance in Wyoming.
The commenter states that the estimation of voluntary compliance rates
is based partly on the fact that ``tanks are likely to be less costly
than pits on smaller and medium volume jobs.'' The commenter states
that without a Federal regulatory backstop, past voluntary compliance
rates and past evidence of job size in particular states do not
guarantee the continued use of tanks in the future.
In response to the foregoing paragraphs in this section, when
issuing the 2015 rule, the BLM acknowledged that it already had ``an
extensive process in place to ensure that operators conduct oil and gas
operations in an environmentally sound manner that protects resources''
(80 FR 16133). At that time, the BLM also noted that while ``the
regulations and Onshore Orders that have been in place to this point
have served to provide reasonable certainty of environmentally
responsible development of oil and gas resources . . .,'' the 2015 rule
``will complement these existing rules by providing further assurance''
that hydraulic fracturing operations are conducted in an
environmentally responsible manner across all public and Indian lands
(id. at 16137). However, as previously noted, in accordance with
Executive Order 13783 and Secretarial Order No. 3349, the BLM recently
conducted a review of the 2015 rule, existing state laws and
regulations, existing Federal authorities and recent incident reports
submitted to the BLM for Federal and Indian oil and gas operations. As
a result of this review, the BLM now believes that the 2015 rule
imposes unnecessary and unjustified compliance costs and burdens.
Moreover, in light of state regulatory programs, the sovereignty of
tribes to regulate oil and gas operations on their lands, and the BLM's
pre-existing regulations and Onshore Oil and Gas Orders and other
Federal authorities, the rescission of the 2015 rule will not lead to
poorly regulated oil and gas development activities, including
hydraulic fracturing operations, on Federal and Indian lands. State
regulatory programs can more readily address local conditions than may
the BLM's rules. Thus, the fact that state rules differ from each other
and are not identical to the 2015 rule do not render state programs
ineffective, or the
[[Page 61938]]
2015 rule essential. Furthermore, as expressed in the Executive Orders,
it is this Administration's policy to reduce unnecessary regulatory
burdens on energy development. Based on the rarity of adverse
environmental impacts that have occurred from hydraulic fracturing
operations before the 2015 rule, and the lack of compelling evidence
that state regulatory programs are inadequate, the 2015 rule is a
duplicative layer of Federal regulation that should be rescinded. To
the extent that the comments address the pre-2015 rule requirements for
prior approval of ``nonroutine fracturing jobs,'' see the BLM's
response to comments in the Rule Authorities section above. As
previously discussed, the BLM has decided not to restore the
requirements for ``nonroutine fracturing jobs'' in 43 CFR 3162.3-2(a).
One commenter states that the proposed rescission of the 2015 rule
does not provide substantive evidence that industry practice is
sufficient to prevent the pollution and degradation of hydrological
resources on public lands. The commenter states that, given its self-
described mandate to provide bona fide minimum standards to ensure
industry compliance, as well as its obligations under NEPA, the BLM
should not rescind protections given to groundwater in the 2015 Rule.
While industry practices can and often do work to appreciably
reduce the risks associated with oil and gas development, the BLM does
not solely rely on industry practice to ensure that oil and gas
development operations on public lands are conducted in an
environmentally responsible manner. Operators on Federal lands must
comply with all Federal, state, and local requirements. On Indian
lands, they must comply with all Federal and tribal permitting and
reporting requirements. As previously noted, the BLM has an extensive
process in place to ensure that operators conduct oil and gas
operations in a safe and environmentally sound manner that protects
resources. The environmental reviews conducted under NEPA provide an
opportunity for the BLM to consider and mitigate potentially adverse
environmental impacts, including those involving hydrological
resources. If hydrological concerns arise during the BLM's review of a
specific oil and gas proposal, the BLM may require additional
information, or impose protective measures, such as lease stipulations
or COAs attached to APDs, to mitigate the potential adverse impacts.
One comment disapproves of the proposed rescission because of a
lack of reasonable regulation in Idaho to protect the communities
impacted by hydraulic fracturing. The commenter adds that there is a
lack of standardization in incident reporting processes in different
states by highlighting a peer-reviewed study published in February 2017
in the Journal of American Chemical Society entitled, ``Unconventional
Oil and Gas Spills: Risks, Mitigation Priorities, and State Reporting
Requirements.'' The study points out differences in reporting
requirements in each of the four states that produce most oil and gas
using hydraulic fracturing, and documents a total of 6,648 spills
between 2005 and 2014.
Contrary to the commenter's assertion, the BLM reviewed the
applicable Idaho state laws and regulations and found an extensive
regulatory framework for addressing the risks associated with hydraulic
fracturing. See Idaho Admin. Code Sec. Sec. 20.07.02.210 and
20.07.02.211. As previously discussed, the fact that state regulatory
programs differ from each other and are not identical to the 2015 rule
does not render the state programs ineffective, or the 2015 rule
essential. Furthermore, operators on Federal or Indian lands are
required to report adverse incidents directly to the BLM. The BLM
requires operators to clean up spills promptly and thoroughly. Those
requirements will not change with the rescission of the 2015 rule.
Multiple commenters asserted that the hydraulic fracturing
regulations of specific states are adequate, and thus the 2015 rule is
not needed. One commenter highlighted that there has never been a
mechanical failure in North Dakota since the North Dakota Industrial
Commission's hydraulic fracturing regulations were implemented; a
separate commenter asserts that the regulatory oversight provided by
the State of North Dakota protects the environment while providing
permitting in a careful but timely manner. Another commenter suggested
that, in Wyoming, operators have employed hydraulic fracturing
technology safely and efficiently for decades. Another commenter
asserts that New Mexico's hydraulic fracturing rules and regulations
are protective of the environment and that hydraulic fracturing is
proficiently regulated by the State of New Mexico, including rigorous
protocols for casing, cementing, completions, recompletions and all
associated procedures, including extensive monitoring and pressure-
testing requirements, as well as mechanical and pressure-based well
integrity testing. That commenter states that adding an additional
layer of Federal regulation on top of an efficient and effective set of
existing state regulations will provide no additional environmental
protection. Additionally, one commenter states that the State of Utah
has an effective regulatory program that, for many years, has
successfully monitored the construction and operation of oil and gas
wells, including well completion operations, such as hydraulic
fracturing, water management, and chemical disclosure. Another
commenter also asserts that Colorado rules and regulations along with
the Memorandum of Agreement with the BLM (and the United States Forest
Service) for Permitting of Oil and Gas Operations on BLM and National
Forest Service Lands in Colorado should suffice in coordinating the
permitting of oil and gas operations on Federal lands. One commenter
states that, in Oklahoma, regulators live in the communities most
affected, are in touch with evolving technical and scientific data, and
have a demonstrated track record of working effectively with industry
as well as the other stakeholders of public and private lands. In
addition, a commenter asserts that Western States with oil and gas
production have robust regulations to protect the environment and
public health and are best-equipped to regulate oil and gas
development. The commenter asserts that the Western States have
experienced few, if any, adverse impacts involving water quality and
water allocation attributable to hydraulic fracturing and that the
process has been used for more than a million wells for over sixty
years, and is responsible for increasing the nation's ability to
recover oil and gas at great economic benefit.
The BLM thanks the commenters for providing comments and supporting
information.
One commenter states that the EA for the 2017 proposed rule reveals
that misguided public sentiment regarding hydraulic fracturing was a
lead motivator for the BLM's initiation of rulemaking in 2010. The
commenter states that BLM also accurately observed that adverse
environmental impacts from hydraulic fracturing were a rare occurrence
prior to the final 2015 rule, and that observation remains true today.
The commenter asserts that, instead of imposing a costly regulatory
burden on oil and gas operators, the BLM would be better served by
dedicating resources to countering these unfounded public concerns.
The BLM agrees that the 2015 rule imposes compliance costs on the
oil and gas industry that are no longer justified. The remaining
statements in this
[[Page 61939]]
comment are outside the scope of this rulemaking.
One commenter states that the 2015 rule would have required that
all fluids recovered between the commencement of hydraulic fracturing
operations and the authorized officer's approval of a produced water
disposal plan under BLM requirements must be stored in rigid enclosed,
covered, or netted and screened above-ground tanks. The commenter
further states that no regulatory mechanism exists for the ``approval
of a produced water disposal plan'' on an individual well basis, thus
the limitations the 2015 rule purports to apply to recovered fluids
storage are premised on an administrative approval process that does
not exist.
As this final rule rescinds the 2015 rule, this comment is outside
the scope of the present rulemaking action.
Adequacy of Tribal Regulations
Multiple commenters state that the BLM's suggestion that the 2015
rule is ``duplicative'' of existing tribal regulation is unsupported.
The commenters state that the differences between the 2015 BLM rule and
other regulations are even greater on Indian lands, where many tribes
have not developed their own regulatory programs to manage
hydraulically-fractured oil and gas development. The commenters state
that this is acknowledged in the EA. Another commenter asserts that
relying on state regulations is inadequate for protecting tribes. One
commenter describes experiencing multiple oil spills related to
injection wells on tribal lands and the lack of resources to respond
and hold corporations accountable for the injury, damage, and
unnecessary burden the oil industry placed on the tribe and its
resources. The commenter states that, even though the sovereignty of
tribes to regulate operations on their lands may be an option and
reality for some tribes, others have yet to develop the capacity to
enforce such regulations on their lands and may never have the
resources to effectively manage and enforce oil and gas regulations.
The 2015 rule would directly benefit and help protect these tribes.
We acknowledge that not all oil and gas producing tribes have
exercised their sovereignty to regulate hydraulic fracturing
activities. Rescission of the 2015 rule, however, does not affect those
tribes' options for promulgating and implementing programs in exercise
of their self-governance and sovereignty. In addition, the BLM
regulations applicable to tribal lands, which include the regulations
at 43 CFR subpart 3162, as amended by this final rule, and Onshore Oil
and Gas Orders 1, 2, and 7, reduce the risks associated with hydraulic
fracturing by providing specific requirements for well permitting;
construction, casing, and cementing; and disposal of produced water.
These BLM regulations, along with the enforcement mechanisms that are
available to the BLM on tribal lands, provide reasonable assurance that
oil and gas development on tribal lands will occur in an
environmentally responsible manner, even when tribal regulations or
enforcement mechanisms to ensure responsible oil and gas development
are not fully developed.
Rule Process
Multiple commenters assert that the BLM has failed to explain why
the 2015 rule is no longer needed to ensure the environmentally
responsible development of Federal oil and gas resources. These
commenters note that the Supreme Court has outlined procedures that an
agency must take to comply with the Administrative Procedure Act (APA)
when changing an existing regulation, including the need to provide a
reasoned analysis or reasoned explanation for the change. The
commenters contend that the BLM's 2017 proposed rule does not meet
these requirements and is fraught with loose language that does not
demonstrate a reasoned basis or reasoned explanation for the change.
Some commenters assert that the BLM's decision to rely on Executive
Order 13783 and Secretarial Order 3349 to justify the proposed
rescission fails to provide the ``reasoned explanation'' required by
the APA. These commenters note that Executive Order 13783 directs
agencies to review regulations that ``unduly burden the development of
domestic energy resources beyond the degree necessary to protect the
public interest or otherwise comply with the law.'' They contend that
the BLM does not explain why the 2015 rule ``burdens'' the development
of energy resources as defined by the Executive Order, particularly in
light of the BLM's findings that the 2015 rule would cost just a small
fraction of a percent of the profit margins of small operations. The
commenters further state that the proposed rescission does not address
other provisions of the Executive Order, including that ``all agencies
should take appropriate actions to promote clean air and clean water
for the American people.''
Finally, some commenters state that the BLM articulated a reasoned
justification in 2015 for the storage tank requirement, and that the
agency now proposes to rescind that same requirement without addressing
the evidence from the 2015 record or offering any explanation for why a
tank requirement would no longer deliver important environmental
benefits.
On the contrary, the BLM believes that it has articulated a
reasoned justification for rescinding the 2015 final rule. It therefore
has not changed this final rule based on these comments. The Supreme
Court has explained that ``[a]gencies are free to change their existing
policies as long as they provide a reasoned explanation for the
change,'' ``display awareness that [they are] changing position,'' and
``show that there are good reasons for the new policy.'' Encino
Motorcars, LLC v. Navarro, __U.S. __, 136 S. Ct. 2117, 2125-26 (2016).
However, agencies do not need to show ``that the reasons for the new
policy are better than the reasons for the old one'' or necessarily
``provide a more detailed justification than what would suffice for a
new policy created on a blank slate.'' FCC v. Fox Television Stations,
Inc., 556 U.S. 502, 515 (2009).
The BLM has provided a reasoned explanation for rescinding the 2015
rule that accords with these requirements: The BLM believes that the
2015 rule, which would impose compliance costs and information
requirements that are duplicative of regulatory programs of many states
and some tribes, is redundant and therefore unnecessarily burdensome on
regulated entities. Any marginal benefits provided by the 2015 rule do
not outweigh the rule's costs, even if those costs are a small
percentage of the cost of a well. In fact, benefits were largely
unquantified in the 2015 rule. The BLM has also provided good reasons
for its new policy, explaining that state regulatory programs
(including those of the states with most of the Federal oil and gas
leasing), the sovereignty of tribes to regulate operations on their
lands, and other preexisting Federal regulations provide a better
framework than the 2015 rule for mitigating the impacts associated with
hydraulic fracturing operations. For example, there are currently laws
or regulations to address hydraulic fracturing in all 32 of the states
in which the BLM currently manages oil and gas leases, and the BLM has
several existing requirements, some of which are set out at 43 CFR
3162.3-1 and in Onshore Oil and Gas Orders 1, 2, and 7, that allow it
to reduce the risks associated with hydraulic fracturing. Additionally,
the BLM has explained that rescinding the 2015 rule's storage tank
requirement may alleviate some on-the-ground indirect impacts, such as
[[Page 61940]]
those associated with truck traffic to transport tanks to and from well
sites.
The BLM is not required to demonstrate that its reasons for
rescinding the 2015 rule are better than or refute its rationale for
initially promulgating the 2015 rule. This is especially true where, as
here, the 2015 rule was never operational and did not engender serious
reliance interests on the part of the regulated community. By providing
an explanation for why it is rescinding the 2015 rule and demonstrating
that there are good reasons for relying on state regulations, tribal
sovereignty, and the BLM's preexisting regulations, the BLM has
provided the necessary justification for changing its policy regarding
the regulation of hydraulic fracturing. Furthermore, there is no legal
impediment to this Administration implementing its policies and
priorities through rulemaking to rescind or amend existing regulations.
Some commenters state that the BLM failed to consider a full range
of alternatives in its environmental assessment. In particular, the
commenters state that the BLM should have analyzed alternatives that
strengthen the rule instead of rescinding it, including alternatives
that regulate stimulation operations broadly, area of review,
strengthen frack hit protections, baseline water testing, well
construction, and restricted chemicals.
The BLM disagrees. The BLM considered a reasonable range of
alternatives in its environmental assessment in light of the proposed
action's purpose and need and the environmental effects that may result
from rescinding the 2015 final rule. NEPA requires an agency to analyze
all reasonable alternatives related to the purposes of the agency's
action. Where, as here, an agency prepares an EA, the range of
alternatives that the agency must consider, and the degree of analysis
that is required, is less than is required for environmental impact
statements. Moreover, ```the range of alternatives that [an] agency
must consider [in an EA] decreases as the proposed action's
environmental impact becomes less and less substantial,' '' Earth
Island Inst. v. United States Forest Serv., 697 F.3d 1010, 1023 (9th
Cir. 2012) (quoting Louisiana Crawfish Producers Ass'n-West v. U.S.
Army Corps of Engineers, 463 F.3d 352, 356-57 (5th Cir. 2006)
(alterations omitted)), and it becomes even more diminished where, as
here, an agency concludes that the action being considered will have a
minimal environmental effect. See Save Our Cumberland Mts. v.
Kempthorne, 453 F.3d 334, 342-43 (6th Cir. 2006). Furthermore, although
the unsigned draft EA accompanying the proposed rulemaking analyzed
only two alternatives, the signed EA for this final rule analyzes four
alternatives, and explains why other alternatives were considered but
not carried forward for analysis.
As described in detail above, this final rule will have minimal
environmental effects. It will not authorize hydraulic fracturing
operations as a whole, it will not authorize any particular hydraulic
fracturing operation on Federal or Indian lands, and it will not impact
the overall number of hydraulic fracturing operations on Federal or
Indian lands. What few impacts may result from the final rule will be
mitigated by state and tribal regulations and the preexisting Federal
regulations. In light of these minimal impacts, the BLM did not need to
analyze additional alternatives beyond the alternative that were
analyzed in the EA that has been prepared for this final rule.
Additionally, the commenters are mistaken that the BLM should have
analyzed alternatives that strengthened the 2015 final rule. The
purpose and need of a proposed action determines the universe of
alternatives that an agency must consider. The purpose of the BLM's
proposed action (the 2017 prosed rule) ``is to reduce and eliminate
unnecessary regulatory requirements in order to more efficiently manage
oil and gas operations,'' and the need is ``to more prudently balance
the BLM's interest in mitigating the risks of oil and gas development
operations, including hydraulic fracturing, . . . with the compliance
burdens it imposes on the oil and gas industry.'' Alternatives that
would retain or increase the regulatory burdens imposed by the 2015
final rule on the oil and gas industry would not further the BLM's
purpose and need for action and, therefore, did not have to be
analyzed.
Some commenters assert that the BLM's proposed rescission of the
2015 rule fails to comply with NEPA. These commenters state that the EA
prepared by the BLM contains only a brief discussion of a few of the
impacts related to groundwater, surface water, and greenhouse gas
emissions, which it determines to be insignificant. The commenters
contend that these determinations contradict those found in the EA that
the BLM prepared when it promulgated the 2015 rule, ignore recent
science regarding hydraulic fracturing, and contradict several reviews
of hydraulic fracturing conducted in California and elsewhere that
demonstrate the potential for other significant environmental impacts
that may result from the repeal of the 2015 rule.
The BLM disagrees with the commenters that the EA's discussion of
impacts constituted a NEPA violation. Pursuant to CEQ's regulations
implementing NEPA, an EA needs to include only ``brief discussions . .
. of the environmental impacts of the proposed action and
alternatives.'' (See 40 CFR 1508.9(b).) The EA's discussion of the
impacts related to groundwater, surface water, and greenhouse gas
emissions satisfies this requirement. Moreover, BLM notes that the EA
references appropriate portions of the 2015 EA addressing these
impacts, incorporating them into this EA.
Similarly, the BLM disagrees with the commenters that its
determinations that the impacts to groundwater, surface water, and
greenhouse gas emissions of this final rule are insignificant
contradict its determinations in the EA prepared for the 2015 rule.
With regard to surface water and groundwater, the 2015 EA merely stated
that, under the No Action Alternative (i.e., existing regulations), the
impacts to surface water and groundwater described in the EA would be
ongoing. The 2015 EA neither stated nor concluded that the impacts to
those resources from the No Action alternative would be significant.
Similarly, there is no contradiction between the two EAs regarding
impacts related to greenhouse gas emissions. The 2015 EA did not, as
the commenters suggest, determine that greenhouse gas emissions related
to the No Action alternative would be significant. On the contrary, the
2015 EA found that although ``the various action alternatives would
result in some small variations in [greenhouse gas emissions],'' none
of them ``would appreciably affect the amount of GHG emissions arising
from oil and gas operations on Federal and tribal lands as compared to
[existing regulations].'' This finding is consistent with the BLM's
current determination that rescinding the 2015 final rule would not
result in an appreciable increase in greenhouse gas emissions.
The BLM also disagrees that the determinations in the EA ignores
recent science regarding hydraulic fracturing. The BLM reviewed and
considered a wide range of scientific evidence, including recent
studies, in assessing the environmental impacts associated with
rescinding the 2015 final rule. For example, the BLM gave considerable
weight to the EPA's December 2016 study of hydraulic fracturing's
potential impact on drinking water resources. NEPA, however, does not
require the BLM to rely equally on all such studies.
[[Page 61941]]
Rather, NEPA permits agencies to rely on their expertise to determine
which studies are particularly relevant or scientifically accurate. The
fact that the EA does not specifically address the findings in the
studies referenced in the comment does not mean that such studies were
not considered. It simply means that, in analyzing the impacts
associated with rescinding the 2015 final rule, the BLM found other
studies more relevant.
Some commenters assert that the BLM violated NEPA by basing its EA
on unfounded assumptions rather than sufficient evidence or analysis.
The commenter states, for example, while acknowledging potential risks
from the impacts that it did consider, the BLM finds that existing
state and tribal regulations and the BLM's existing authorities will
``allow it to reduce the risks associated with hydraulic fracturing.''
However, the commenter states, the 2015 final rule remains more
comprehensive than the requirements in many states and tribes, and the
BLM has previously stated that the final rule ``would result in a
reduction of the risks associated with hydraulic fracturing operations
on Federal and Indian lands.''
The commenters are mistaken. The BLM based its EA on evidence,
analysis, and technical expertise, not unfounded assumptions. For
example, the specific conclusion referenced by the commenters that
existing regulatory frameworks will allow the BLM to reduce the risks
associated with hydraulic fracturing is based on the BLM's detailed
review of state, tribal, and Federal regulations. See RIA at Sec.
2.12, and EA at Appendix 1. That review indicated that all 32 states
with existing Federal oil and gas leases currently have regulations to
address hydraulic fracturing operations, as do some tribes with oil and
gas resources. Additionally, the BLM has several existing requirements,
some of which are set out at 43 CFR subpart 3162 and in Onshore Oil and
Gas Orders 1, 2, and 7, that allow it to reduce the risks associated
with oil and gas operations, including those of hydraulic fracturing.
The BLM also possesses discretionary authority allowing it to impose
site-specific protective measures reducing the risks associated with
hydraulic fracturing. Relying on this evidence to conclude that the
2015 final rule was duplicative of an existing regulatory framework
that will reduce the risks associated with hydraulic fracturing
operations is a technical judgment within the BLM's area of expertise.
The BLM may rely on the judgment of its own experts, see San Juan
Citizens Alliance v. Stiles, 654 F.3d 1038, 1057 (10th Cir. 2011), even
if the same regulatory framework would have led the commenters to
arrive at a different conclusion. See Greater Yellowstone Coal. v.
Flowers, 359 F.3d 1257, 1271 n. 14 (10th Cir. 2004).
The commenters are also mistaken that the 2015 rule's potential to
reduce risks somehow calls into question the BLM's conclusion that it
can rely on state, tribal, and Federal regulatory framework to reduce
the risks associated with hydraulic fracturing operations. The 2015
rule was meant to ``add to'' and ``complement'' this existing
regulatory framework. (80 FR 16128). Regardless of whether those
additions would have resulted in additional risk reductions, the BLM's
conclusion that the existing regulatory framework is capable of
reducing risks remains valid.
Some commenters assert that the BLM must prepare a full EIS before
rescinding the 2015 rule.
The BLM has not prepared an EIS in response to those comments. NEPA
requires an agency to prepare an EIS when it proposes to take a major
Federal action that significantly affects the quality of the human
environment. Agencies must consider the context of the action and the
intensity of its impacts to determine whether an action significantly
affects the quality of the environment. As discussed in the BLM's EA
and FONSI, the BLM considered the context of rescinding the 2015 rule
and determined that doing so would remove information requirements that
are duplicative of the regulatory programs of many states and some
tribes with active oil and gas development. The BLM also considered the
intensity, as that term is defined in CEQ's NEPA regulations, of
rescinding the 2015 final rule. Applying the intensity factors listed
in 40 CFR 1508.27(b), the BLM determined that rescinding the 2015 rule
would not have a severe impact on the quality of the human environment.
Based on its considerations of the context and intensity of the
proposed action, the BLM determined that rescinding the 2015 rule will
not significantly affect the quality of the human environment. In light
of that determination, it is unnecessary to prepare a full EIS before
rescinding the 2015 rule.
Some commenters assert that the BLM failed to analyze indirect and
cumulative impacts of rescinding the 2015 rule.
Agencies are required to analyze the indirect and cumulative
impacts associated with a proposed action. The BLM's analysis of those
impacts is set forth, respectively, in sections 4.0 and 5.0 of the EA.
One commenter states that ESA and NHPA consultations are required
before the 2015 final rule can be rescinded.
The ESA requires an agency to consult with the U.S. Fish and
Wildlife Service or National Marine Fisheries Service to ensure that
any action it authorizes, funds, or carries out is not likely to
jeopardize the continued existence of any listed species or result in
the destruction or adverse modification of critical habitat. Section
106 of the NHPA requires Federal agencies to take into account the
effects of their undertakings on historic properties included on or
eligible for inclusion on the National Historic Register of Historic
Places (NRHP), and to afford the Advisory Council on Historic
Preservation a reasonable opportunity to comment on such undertakings.
The BLM is not required to perform ESA or NHPA consultations to
rescind the 2015 rule. Neither the rescission nor implementation of the
2015 rule would, by themselves, authorize or prohibit hydraulic
fracturing operations as a whole, or any particular hydraulic
fracturing operation on Federal or Indian lands. These actions are also
not expected to impact the number of hydraulic fracturing operations.
As such, the actions would not, by themselves, have an effect on any
listed species or its habitat nor any historic properties that are
listed on or eligible for listing on the NRHP. After the 2015 rule is
rescinded, the BLM will continue to make decisions involving the
development of oil and gas resources on BLM-administered lands at the
land use planning, leasing, and permitting stages in compliance with
NEPA, the ESA, and the NHPA. Indeed, site-specific proposals to drill
for and develop oil and gas resources that involve hydraulic fracturing
operations would require the same level of compliance with the ESA and
NHPA if the BLM did not rescind the 2015 rule. Given that the BLM
considers the cumulative and site-specific effects of proposed oil and
gas operations as part of its land use planning, leasing, and
permitting processes, as is discussed earlier in this preamble, and
will conduct appropriate consultations whenever and wherever
appropriate, consultation under the ESA and NHPA is not required at
this time.
Some commenters state that, because the issue of ``frack hits'' was
not part of the discussions between stakeholders and the agency during
the rulemaking process for the 2015 rule, it is reasonable that the BLM
would rescind the 2015 rule and defer issuance of any
[[Page 61942]]
rule related to ``frack hits'' until the appropriate regulatory
procedures are invoked.
Some commenters also state that the 2015 rule would have required
that before hydraulic fracturing operations begin, the operator must
perform a successful mechanical integrity test of any casing or
fracturing string through which the operation will be conducted. These
commenters contend that the administrative record prepared for the 2015
final rule ``does not contain comments regarding the efficacy, cost, or
purpose of testing the lateral portion of the wellbore because that
requirement was not part of the proposed rule.''
The commenters contend that measures to protect against ``frack
hits'' and requiring mechanical integrity tests included in the 2015
rule were not logical outgrowths of the BLM's proposed rule. Because
the BLM is rescinding the 2015 rule, and because the present rule
rescission does not contain measures related to ``frack hits'' or
require mechanical integrity tests, it is unnecessary to address
whether the issues of ``frack hits'' and mechanical integrity tests are
a logical outgrowth of the proposed rule that the BLM published.
One commenter states that it is impossible to reconcile a
requirement to conduct a mechanical integrity test on casing that does
not protect usable water and it is likely to increase costs of
completing a well by $75,000 to $100,000. Given the absence of any
benefit that will be derived from these costs, rescission of the 2015
rule is reasonable and appropriate.
The BLM agrees that rescission of the 2015 rule is appropriate and
good policy.
Costs of 2015 Rule and Effects on Industry
Multiple commenters state that the 2015 rule would not be
burdensome for industry. One commenter states that there are several
problems with BLM's assertion that the 2015 rule ``imposes burdensome
reporting requirements and other unjustified costs on the oil and gas
industry'' (82 FR 34464). The commenter states first, that the BLM's
own RIA finds that the 2015 rule would cost approximately $9,690 per
well, or about 0.1 percent to 0.2 percent of the cost of drilling a
well (RIA at 3, Tables 4.2.2.a, 4.2.2.b). The commenter further notes
that the BLM's estimate of the costs of the 2015 rule have not
substantially changed since 2015 (80 FR 16,130 (estimating compliance
costs to be ``approximately 0.13 to 0.21 percent of the cost of
drilling a well'')). The commenter states that BLM also noted that its
cost estimates may be overstated where industry is already in
compliance.
In the RIA for the 2015 rule, the BLM asserted that regulation
would result in a reduction of the risks associated with hydraulic
fracturing operations on Federal and Indian lands, without providing an
estimate for the monetary benefits of this risk reduction. The BLM
noted in the 2015 RIA that the majority of the requirements were
consistent with industry practice and that some were required by state
regulations or were generally addressed by existing BLM requirements.
In light of the protections available under other Federal regulations,
the increased prevalence of state and tribal laws and regulations to
address hydraulic fracturing, and new industry practices, the BLM
believes that the requirements imposed by the 2015 rule are redundant
and therefore unnecessarily burdensome. There were no monetary
estimates of any incremental benefit that the 2015 rule provides in
addition to existing Federal, state, and tribal regulations and
industry standards. Such incremental benefits, however, are likely to
be too small in light of the increased prevalence and comprehensiveness
of these standards since the original RIA was published to justify
compliance costs that are both monetized and certain to exist.
One commenter notes that, in 2015, in response to commenters'
arguments that the rule was not economically justified and that
benefits did not exceed costs, the BLM responded that the 2015 rule was
``prudent,'' ``necessary,'' and ``common-sense,'' and that the rule's
``burden should be minimal.'' The commenter asserts that, in its
proposed rescission, the BLM never sufficiently explains why those same
prudent, common-sense requirements, deemed necessary to environmental
protection after weighing compliance costs, are now suddenly
unnecessary.
As noted in previous responses, in light of the protections
available under other Federal regulations, the increased prevalence of
state and tribal laws and regulations to address hydraulic fracturing,
and new industry practices, the BLM now believes that the requirements
imposed by the 2015 final rule are redundant or only marginally
beneficial, and therefore unnecessarily burdensome.
One commenter states that the BLM fails to acknowledge the forgone
cost savings of the tank requirement that will partly offset any
estimated cost savings from the rescission. The commenter notes that
storage tank requirement from the 2015 rule was anticipated to generate
long-term cost savings for industry that would have partly offset their
compliance costs. The commenter suggests that rescinding the
requirement will forgo those cost savings, and that loss of cost
savings will partly offset any positive cost savings anticipated from
the rescission.
In response to the previous comment, the BLM notes that it is not
clear that requiring operators to use storage tanks for flowback and
produced water would generate any cost savings. Operators that instead
use central reservoirs may have decided to do so precisely because it
is the most cost-effective option available to them, and requiring them
to do otherwise may have the unintended consequence of increasing costs
for them.
One commenter states that an unanticipated cost associated with
rescinding the 2015 rule is related to road and infrastructure damage
associated with trucks hauling large quantities of salt water and
drilling mud at load weights exceeding legal limits by 35 percent. The
commenter offers that Texas has incurred more than $2 billion debt to
repair about 40 percent of their damaged roads in absence of having a
dedicated revenue source to pay for it. A commenter states that failure
to hold businesses accountable for their externalities amounts to
indirect subsidies, which is not fair to producers of clean energy who
do not receive these advantages. The commenter states that Federal
lands are leased to these extractors at prices that are well below
market values for extraction on private lands. The commenter asserts
that this is another indirect subsidy for the extractors and is a bad
deal for the taxpayers.
The use of public roads for the transport of materials and
equipment both to and from energy production sites, including weight
restrictions and taxation, is regulated by states and localities, and
on tribal lands by tribes. It was not addressed in the 2015 rule, and
thus is outside the scope of this rulemaking. Operators do need BLM's
approval for access roads from public roads across public lands to
their operation sites.
The BLM also disagrees with the assertion that Federal lands are
leased at ``well below market values'' for oil and gas extraction on
comparable private lands. Although private leases may often have higher
royalty rates, there are often greater regulatory burdens uniquely
associated with Federal leasing requirements. These include NEPA
reviews for leasing nominations and drilling permits, production
[[Page 61943]]
measurement compliance requirements, and other fees and assessments,
that operators do not encounter to the same extent on non-Federal
lands. A simple comparison of royalty rates between Federal and non-
Federal oil and gas leases is insufficient to support the commenter's
conclusion about market values. Furthermore, bonus bids, rentals and
royalties are outside the scope of this rulemaking.
One commenter suggests that California's growing economy is an
example to counter industry's claims that the 2015 rule and regulations
in general, unnecessarily encumber energy production, constrain
economic growth, and prevent job creation.
The commenter does not provide evidence that regulation of
hydraulic fracturing in California specifically has an impact on
statewide economic growth. Also, different states have different mixes
of industries and employers, as well as different geology, land
ownership patterns, and other conditions important to business growth.
Thus, we have no reasonable basis to extrapolate from any state's
economic growth to a conclusion that the 2015 rule would be a net
benefit for job creation.
One commenter suggested it is valuable to have a unified standard
with which to regulate hydraulic fracturing. The commenter states that
frack hits also pose a threat to industry profits, as they may also
lead to a decrease in well production. The commenter states that,
without firmly regulating irresponsible drilling practices, we run the
risk of not only damaging the ecological health of our public lands and
water resources, but also sabotaging the success of the extractive
industry.
As noted in the RIA, the American Petroleum Institute does provide
uniform, national voluntary standards for conducting hydraulic
fracturing. Hydraulic fracturing oversight is and will continue to be
provided through the state laws and regulations detailed in API 100-1
and API 100-2. There is ample evidence from national production data
that hydraulic fracturing allows oil and gas production that would not
otherwise be realized. Any frack hits on neighboring wells from using
the technology are unfortunate but not nationally significant compared
to the overall industry growth emanating from this technology.
One commenter suggests that, because the 2015 rule presented
significant conflicts with existing Federal and state regulations, its
adoption held the potential to create regulatory uncertainty and
confusion, increasing project costs, thus providing further
disincentives to operators to develop resources on Federal lands that
the agency manages for the American people.
The BLM does not agree that regulations that are largely consistent
with state rules and industry practices necessarily increase
uncertainty or confusion. The BLM does agree, however, that such
overlap can make such regulations redundant, marginally beneficial, and
unnecessarily burdensome, which is the why it is rescinding the 2015
rule.
Multiple commenters state that additional BLM regulation of a
process already regulated by the states will decrease efficiency and
increase costs. Commenters assert that the BLM does not have the staff,
the budget, or the expertise to process APDs with the same efficiency
as the states. One commenter states that the delay in processing APDs
by the BLM will result in declining production from Federal lands to
the detriment of the public. Another commenter asserts that the BLM
severely underestimated the cost of the 2015 rule by not including the
cost of delays in permit approval. The commenter asserts that if APDs
are not approved in a timely manner, the re-leasing process will cost
additional millions. A separate commenter highlights that BLM officials
conceded that, given the combination of increases in workload
associated with the hydraulic fracturing rule and reductions in the
agency budget, getting the work done could be an issue. The commenter
also notes that, among other problems, the BLM recognizes that ``skills
gaps'' are a ``program vulnerability'' for the BLM's existing oil and
gas programs. The commenter therefore concludes that rescission of the
2015 rule is entirely appropriate given the admonitions of agency
leaders that the BLM does not have the expertise in the field to
administer the rule.
The BLM's engineers and field managers have decades of experience
exercising oversight of these wells during the evolution of hydraulic
fracturing technology. However, as stated in the RIA for this rule, the
BLM recognizes the potential that the 2015 rule might pose unnecessary
delays and implementation costs to the BLM and operators. These costs
were not quantified in the RIA for the 2015 rule. The BLM's staffing
levels, budget and appropriations are outside the scope of this
rulemaking.
One commenter argues that, due to North Dakota's unique history of
land ownership, it is typical for oil and gas spacing units to consist
of a combination of Federal, state, and private mineral ownership. The
commenter notes that, even in circumstances where the Federal mineral
ownership within a spacing unit is small relative to other mineral
ownership, the 2015 rule would have required all the oil and gas
operators within the unit, as a practical matter, to conduct operations
in accordance with the 2015 rule applicable to the development of
Federal minerals. The commenter asserts that complying with the Federal
requirements and permitting timelines imposed by the 2015 final rule
will substantially delay operations on any spacing units that contain
Federal minerals and that this delay adversely affects the development
of all minerals within the unit, including state and private oil and
gas minerals.
As stated in the RIA for this rule, the BLM recognizes the
potential that the 2015 final rule might pose unnecessary delays and
implementation costs to the BLM and operators. We understand the
commenter's concerns that many long directional wells are completed in
many tracts, some Federal, and some not federal. The operators' burdens
of complying with the 2015 rule could adversely affect the owners of
the non-federal tracts. Those concerns support the BLM's decision to
rescind the 2015 rule.
Some commenters state that the 2015 rule would have represented an
expansion of the information that oil and gas developers are required
to disclose publicly both before and after operations and that, much of
this information, and particularly information regarding local geology
and the operators' technical designs for extracting resources from that
geology, is highly proprietary and represents economically valuable
commercial information. The commenters argue that the 2015 rule failed
to account both for the confidential nature of the information the rule
required to be disclosed and the commercial consequences of that
disclosure. The commenters state that, because the 2015 rule would have
required public disclosure of highly confidential and commercially
valuable information, it is contrary to Federal public records law and
its rescission is appropriate. Another commenter argued that the same
requirement of the 2015 rule failed to account for service companies
owning the trade secrets.
As the commenter notes, by rescinding the 2015 rule, the BLM would
no longer require that the operator submit information to the BLM and/
or FracFocus after the hydraulic fracturing operation is complete. As
[[Page 61944]]
stated in the RIA, the removal of this requirement would alleviate some
administrative burden. At least for Federal wells, operators are likely
to report the chemicals used regardless of whether the BLM requires
them to or not, since almost all states currently have chemical
disclosure requirements.
One commenter estimates that the 2015 rule would have imposed a
minimum per-well additional cost of $1,500 associated with assembling,
analyzing and adding new information to APDs and final reports
submitted to the BLM, not including the potential additional costs
associated with legal review and requirements for the operator to
verify and manage proprietary information that is claimed to be exempt
from disclosure. The commenter estimates the following additional costs
of the 2015 rule: Potential work stoppage during completions if there
is a ``false positive'' 500 psi increase in annulus pressure (assumed
$200,000 to $500,000 per day standby cost); managing ``recovered
fluids'' or produced water by constructing and utilizing a central
storage and treatment facility according to rule requirements
(estimated 5-year net present cost of $2.3 million for a lined pit, vs.
$23 million for using 500-barrel tanks to provide a storage capacity of
250,000 barrels); concern that a BLM field office could interpret the
2015 rule in a more stringent fashion than intended, which could lead
to a slowdown, stoppage, or delay of work, or additional costs for
specific requirements.
The BLM acknowledges that there are several potential compliance
costs for the 2015 rule that it did not quantify in the economic
analysis that was prepared for that rule. However, because this final
rule rescinds the 2015 rule, it is not necessary to review whether the
BLM's cost estimates for that rule were adequate, or to determine if
the commenters' estimates are appropriate.
A commenter critiqued the effects of the 2015 rule on operators,
concluding that the rule would have caused unintended burdens or
delays.
Because we are rescinding the 2015 rule, there is no need to
analyze the commenters' predictions.
One commenter asserts that small businesses will benefit from this
final rule because elimination of the 2015 rule would eliminate any
future possibility that they must pay the compliance costs associated
with the rule.
We agree that small businesses would benefit to the degree that
they are no longer subject to the compliance costs associated with the
2015 rule.
One commenter states that a comprehensive analysis of the costs the
2015 rule would have imposed demonstrates that costs savings resulting
from the rule's rescission are likely to exceed $220 million per year
due to increased administrative costs ($17.8M), delay costs ($6.7M),
additional casing costs ($174M), additional mechanical integrity
testing costs ($17M), and additional costs of recovered fuel storage
($4.9M).
The comment has been considered in developing the final regulatory
impact analysis (RIA), but we find that the estimated cost savings
discussed in the RIA are more supportable and are adequate for the
decision to rescind the 2015 rule.
Regional and National Implications
One commenter states that the economic impact of rescinding the
2015 final rule on the outdoor industry and farming should be seriously
considered when evaluating whether rescinding the 2015 rule is good for
economic growth and job creation. The commenter asserts that hydraulic
fracturing operations effectively destroy natural and rural areas
integral to the outdoor industry. The commenter notes that, in 2011,
the outdoor industry employed 6.1 million Americans and Americans spend
approximately $646 billion annually on outdoor recreation.
There is little to no evidence that properly regulated hydraulic
fracturing operations have a significantly greater effect on natural
and rural areas integral to the outdoor industry compared to the
conventional oil and gas drilling operations that have taken place on
BLM lands for decades. In its decision to rescind the 2015 rule, the
BLM examined existing state regulations--as well as existing Federal
regulations contained in Onshore Orders 1, 2, and 7--and determined
that they are sufficient to ensure that hydraulic fracturing operations
on Federal lands remain properly regulated.
To the degree that lands open for oil and gas development could
have an opportunity cost in that they could otherwise be used for
recreational activities, the BLM has long implemented FLPMA's policy of
multiple use that uses the NEPA environmental review process to
determine how best to plan for the public's desires to put the lands to
competing uses. The BLM's land use planning, however, is beyond the
scope of this rulemaking.
Multiple commenters support the proposed rescission asserting that
the 2015 rule imposes unnecessary costs, hinders energy production, and
constrains economic growth. Commenters argue that the potential cost
impacts of the 2015 rule on exploration and production activities on
BLM managed lands would greatly exceed the estimates that the BLM
provided in its original RIA. One commenter asserts that governments
should take care to ensure that any regulations they issue to ensure
safety and protect the environment recognize the economic importance
of, and avoid unduly burdening the use of, hydraulic fracturing to
develop America's energy resources.
In analyzing the 2015 rule, the BLM has reached the same conclusion
regarding its unnecessary costs and impact on energy production and
economic growth. As a result, the BLM has decided to rescind the 2015
rule.
One commenter stated that BLM's 2015 rule would exacerbate the
decline in oil and natural gas production on Federal lands and that
this would have a severe, negative effect on Wyoming's tax revenue and
employment numbers, would increase the costs for energy to all
consumers, and could increase this country's reliance on imports from
less than friendly nations.
Regardless of whether the 2015 rule would have had a ``severe,
negative effect'' on any state, or whether it would have caused an
increase in reliance upon imported oil or gas, the BLM does believe
that the costs of complying with the 2015 rule would be an unnecessary
burden on industry. This Administration's policy is to increase
revenues and to reduce reliance on imported oil through this and other
actions to reduce unnecessary burdens on energy industries, including
oil and gas on Federal and Indian lands. Thus, we are rescinding the
2015 rule.
Climate Change
Some commenters contend that the BLM cannot, in evaluating its
oversight of hydraulic fracturing on the public lands, overlook the
fact that extracting the new oil and gas resources made exploitable by
modern hydraulic fracturing techniques is inconsistent with any
reasonable likelihood of avoiding the most catastrophic effects of
global climate change. Some commenters recommend that the United States
shift toward alternative forms of energy.
Some commenters assert that the BLM must weigh the relative effects
on oil and gas production, supply, markets, and ultimately emissions of
its actions in regulating public lands hydraulic fracturing. The
commenters assert that this must include an assessment of the net
emissions consequences of all
[[Page 61945]]
reasonable alternatives--including implementation of the 2015 hydraulic
fracturing rule, the BLM's proposed rescission of that rule, or an
alternative rule banning public lands hydraulic fracturing.
Those commenters seek a reduction in leasing and production of oil
and gas from Federal and Indian lands with the goal of reducing
emissions of greenhouse gasses. Issues of land use planning, leasing of
parcels, and levels of production from Federal and Indian lands are
beyond the scope of this rulemaking. Hydraulic fracturing was a
technology available to operators on Federal and Indian lands prior to
the promulgation of the 2015 rule, it would have been available had the
2015 rule become effective, and it will be available after promulgation
of this rescission rule. The BLM is committed to compliance with NEPA
at each stage of its decision-making. NEPA does not require the BLM to
consider banning hydraulic fracturing in its analysis of this
rescission rule. As previously stated, the purpose and need for the
rule is to reduce unnecessary burdens on oil and gas production from
Federal and Indian lands. Furthermore, since emission levels from
future hydraulic fracturing operations are necessarily speculative
(because they depend upon geologic, technical, and economic variables,
plus the potential substitution of sources for oil and gas), a
comparison of ``net emissions consequences'' would not provide useful
information to the decision-maker or the public.
The BLM has not made a change from the 2017 proposed rule to this
final rule in response to those comments.
Recommendations
Multiple commenters suggest the BLM should conduct additional
research regarding the impacts of hydraulic fracturing and of
rescinding the 2015 rule, including the impacts of hydraulic fracturing
on drinking water resources and human health. Some commenters assert
that the BLM must thoroughly study the effects of repealing the rule,
including consideration of new circumstances, studies, and information
developed since the rule was adopted. The commenters assert that this
should include, for example, consideration of recent information
regarding connections between disposal of drilling-related waste and
earthquakes, according to some commenters. Moreover, the commenters
state that the BLM must consider the likelihood that the proposed
deregulation will lead to a significant expansion in poorly controlled
oil and gas drilling and hydraulic fracturing and the consequences for
global climate change. Some commenters suggest that the BLM should
consider and adopt a rule that protects public lands, public health,
and the climate by banning hydraulic fracturing altogether on public
lands.
In response to the previous comments, the BLM notes that, in
December 2016, EPA completed its nationwide study of hydraulic
fracturing. U.S. EPA, Hydraulic Fracturing for Oil and Gas: Impacts
from the Hydraulic Fracturing Water Cycle on Drinking Water Resources
in the United States (Final Report), EPA/600/R-16/236F (available at
2016https://cfpub.epa.gov/ncea/hfstudy/recordisplay.cfm?deid=332990).
The BLM has considered the findings in that report. That report
demonstrated that, like most industrial processes, hydraulic fracturing
has the potential to cause the release of pollutants into the
environment, including groundwater resources. A logical conclusion is
that hydraulic fracturing activities should be regulated to control
those risks. It is not clear, however, that the 2015 rule was the best
or only way to regulate hydraulic fracturing on Federal and Indian
lands. Commenters have failed to provide facts demonstrating that the
BLM needs to conduct another study a year after EPA's report. Risks of
induced seismicity from hydraulic fracturing operations are beyond the
scope of this rulemaking. The USGS studies both natural and induced
seismicity. Several USGS publications are listed at https://earthquake.usgs.gov/research/induced/references.php. Those studies show
that induced seismicity from hydraulic fracturing operations is
uncommon, and seems to occur mostly in areas with small percentages of
federally owned minerals. More common is seismicity induced by the
injection of waste fluids for disposal. Those disposal wells, however,
are regulated by states, tribes and the EPA under the Safe Drinking
Water Act, and are beyond the scope of this rulemaking.
This final rule will not lead to poorly regulated drilling of oil
and gas wells on Federal and Indian lands. Drilling operations will
continue to be subject to the BLM's regulations, including Onshore Oil
and Gas Order No. 2, (53 FR 46798, 1988), state regulations on Federal
land, and tribal regulations on tribal lands. We do not believe that
hydraulic fracturing operations will be poorly regulated under the
present rule, with states and tribes taking the lead for regulating
most hydraulic fracturing activities.
As previously explained, we do not believe it is in the national
interest to ban hydraulic fracturing on Federal and Indian lands.
Hydraulic fracturing activities can be conducted in ways that reduce
risks to the environment while providing the benefits of domestically
produced oil and gas, including jobs. Furthermore, a ban on hydraulic
fracturing on Federal and Indian lands would most likely cause
production to move to areas that are not subject to the BLM's
regulations, and have no impact on emissions.
One commenter asserts that the 2015 rule provides for a ``type
well'' to be used for an entire field to satisfy the pre-fracturing
approval requirements. The commenter recommends that the 2015 rule
should be rescinded in its entirety or expanded to allow a type well to
cover an entire county or basin if the geology is substantially
similar.
The commenter is mistaken. The 2015 rule does not mention a ``type
well.'' The present rule rescinds the 2015 rule in its entirety.
The BLM has not made a change from the 2017 proposed rule to this
final rule based on these commenters' recommendations.
Discussion of the Final Rule
As previously discussed in this preamble, the BLM is revising 43
CFR part 3160 to rescind the 2015 rule. The regulatory amendments in
this final rule are identical to those in the proposed rule, except
that the phrase ``perform nonroutine fracturing jobs'' has been removed
from the regulations at 43 CFR 3162.3-2(a). This final rule restores
the regulations in part 3160 of the CFR to exactly as they were before
the 2015 rule, except for changes to those regulations that were made
by other rules published between March 26, 2015 (the date of
publication of the 2015 final rule) and now, and the phrase ``perform
nonroutine fracturing jobs,'' which is not restored to the list of
subsequent operations requiring prior approval in section 3162.3-2(a).
None of the amendments to part 3160 by other rules are relevant to this
rulemaking. See, e.g., 82 FR 83008 (2016). The following section-by-
section analysis discusses returning to the pre-2015 rule regulations.
Section 3160.0-3 Authority
The BLM amends Sec. 3160.0-3 by removing the reference to the
Federal Land Policy and Management Act of 1976, as amended (43 U.S.C.
1701). The 2015 rule added this reference as an administrative matter.
This final rule returns this section to the language it contained
before the 2015 rule and does not have any substantive impact.
[[Page 61946]]
Section 3160.0-5 Definitions
The BLM amends this section by removing several terms that were
added by the 2015 rule and by restoring the definition of ``fresh
water'' that the 2015 rule removed. This final rule removes the
definitions of ``annulus,'' ``bradenhead,'' ``Cement Evaluation Log
(CEL),'' ``confining zone,'' ``hydraulic fracturing,'' ``hydraulic
fracturing fluid,'' ``isolating or to isolate,'' ``master hydraulic
fracturing plan,'' ``proppant,'' and ``usable water.'' The 2015 rule
used those terms in the operating regulations. Since those operating
regulations are rescinded, these terms are no longer necessary in this
definitions section. This final rule restores the previous definition
of ``fresh water'' to the regulations.
Section 3162.3-2 Subsequent Well Operations
This final rule amends Sec. 3162.3-2 by making non-substantive
changes to paragraph (a), which include replacing the word ``must''
with the word ``shall,'' replacing the word ``combine'' with the word
``commingling,'' replacing the word ``convert'' with the word
``conversion,'' and removing the language from the first sentence of
paragraph (a) that the 2015 rule only added to more fully describe Form
3160-5.
In response to comments received, Sec. 3162.3-2(a) of this final
rule does not include the requirement to obtain prior approval to
``perform nonroutine fracturing jobs.'' As previously discussed in this
preamble, as a result of considerable advances in oil and gas
development technology in the last 20 years, hydraulic fracturing
practices that would have been considered ``nonroutine'' when the BLM
originally issued the regulations requiring prior approval for
``nonroutine fracturing jobs'' are now commonly employed and considered
``routine.'' See the ``Rule Authorities'' discussion of comments for
more information about this revision.
The final rule makes non-substantive changes to paragraph (b) of
Sec. 3162.3-2, which include replacing ``using a Sundry Notice and
Report on Well (Form 3160-5)'' with ``on Form 3160-5.''
The final rule restores ``routine fracturing or'' to paragraph (b)
of Sec. 3162.3-2. The 2015 rule removed those words from the list
because it amended Sec. 3162.3-3 to include a detailed listing of
requirements for hydraulic fracturing operations to be approved by the
authorized officer. This final rule removes that requirement from Sec.
3163.3-3, which is discussed below.
Section 3162.3-3 Other Lease Operations
The BLM revises this section by removing language that was added by
the 2015 rule and returning this rule to the exact language it
contained previously. The 2015 rule made substantial changes to this
section and revised the title to read as ``Subsequent well operations;
Hydraulic fracturing.''
Paragraph (a) of this section in the 2015 rule, as reflected in the
2015 edition of the CFR, includes an implementation schedule that the
BLM would have followed to phase in the requirements of the rule, had
the rule gone into effect. Paragraph (b) of this section contains the
performance standard referencing Sec. 3162.5-2(d). Paragraph (c) of
this section would have required prior approval of hydraulic fracturing
operations. Paragraph (d) of this section lists the information that an
operator would have been required to include in a request for approval
of hydraulic fracturing. Paragraph (e) of this section specifies how an
operator would have had to monitor and verify cementing operations
prior to hydraulic fracturing. Paragraph (f) of this section would have
required mechanical integrity testing of the wellbore prior to
hydraulic fracturing. Paragraph (g) of this section would have required
monitoring and recording of annulus pressure during hydraulic
fracturing. Paragraph (h) of this section specifies the requirements
that would have applied for managing recovered fluids until approval of
a permanent water disposal plan. Paragraph (i) of this section
specifies information that an operator would have been required to
provide to the authorized officer after completion of hydraulic
fracturing operations. Paragraph (j) of this section specifies how an
operator could have withheld information from the BLM and the public
about the chemicals used in a hydraulic fracturing operation. Paragraph
(k) of this section describes how the BLM would have approved variances
from the requirements of the 2015 final rule.
For the reasons discussed earlier in this preamble, the BLM
believes this section of the 2015 rule is unnecessarily duplicative and
would impose costs that would not be clearly exceeded by its benefits
and, therefore, removes these 2015 rule provisions and restores the
previous language of the section.
Section 3162.5-2 Control of Wells
The BLM amends paragraph (d) of this section by restoring the term
``fresh water-bearing'' and the phrase ``containing 5,000 ppm or less
of dissolved solids.'' The final rule also restores other non-
substantive provisions that appeared in the previous version of the
regulations.
Good Cause for Immediate Effectiveness
The APA normally requires regulations to become effective no sooner
than 30 days after publication in the Federal Register (5 U.S.C.
553(d)). Nonetheless, the APA allows regulations to go into effect
immediately upon publication when ``a substantive rule grants or
recognizes an exemption or relieves a restriction'' (5 U.S.C.
553(d)(1)). As explained in this preamble, this final rule relieves oil
and gas operators on Federal and Indian lands from the numerous
restrictions and burdens that would be imposed if the 2015 rule were to
go into effect.
The primary purpose of the delayed effective date requirement in
section 553(d) is to give people a reasonable time to prepare to comply
with or take other action with respect to the rule (See Attorney
General's Manual on the Administrative Procedure Act 37 (1947)). As
explained elsewhere in this preamble, the 2015 rule has never been
operational. Therefore, no one requires time to conform their conduct
to avoid the legal consequences of ``violating'' the regulations that
would remain in effect after rescission of the 2015 rule. Even if
persons not subject to the 2015 rule could claim a benefit from a 30-
day effective date, that would not prevent this final rule from
becoming effective immediately upon publication (Independent U.S.
Tanker Owners Comm. v. Skinner, 884 F.2d 587, 591-92 (D.C. Cir. 1989),
cert. denied, 495 U.S. 904 (1990)).
The APA also allows regulations to go into effect immediately upon
publication for ``good cause'' (5 U.S.C. 553(d)(3)). Application of the
good cause exception requires an `` `urgency of conditions coupled with
demonstrated and unavoidable limitations of time,' '' with the
``primary consideration . . . be[ing] the `convenience or necessity of
the people affected' '' (United States v. Gavrilovic, 551 F.2d 1099,
1104 (8th Cir. 1977) (quoting 92 Cong. Rec. 5650-51 (1946) (remarks of
Cong. Walter))). In determining whether to invoke the good cause
exception, an ``agency is required to balance the [public] necessity
for immediate implementation against principles of fundamental fairness
which require that all affected persons be afforded a reasonable time
to prepare for the effective date of its ruling'' (Gavrilovic, 551 F.2d
at 1105).
[[Page 61947]]
The current posture of the litigation related to the 2015 rule
makes it possible that the 2015 rule could become operational within 30
days of the publication of this final rule. Were that to happen, oil
and gas operators--the persons most affected by this final rule--would
have to go to significant expense to comply with the 2015 rule, even
though that rule would be rescinded in a matter of days upon the
effective date of this final rule. Those significant burdens would not
be offset by the de minimus environmental benefits of a few days of
compliance with the 2015 rule. Requiring oil and gas operators to incur
such significant expense to comply with a rule that will be rescinded
in a matter of days would be fundamentally unfair. Thus, there are
urgent conditions, unavoidable limitations of time, and a risk to the
convenience or necessity of the people affected.
For both of these reasons, the BLM finds that there is good cause
for this final rule to be effective upon publication in the Federal
Register.
III. Procedural Matters
Regulatory Planning and Review (Executive Orders 12866, 13563, and
13771)
Executive Order 12866 provides that the Office of Information and
Regulatory Affairs in the Office of Management and Budget will review
all significant rules. The Office of Information and Regulatory Affairs
has determined that this rule is significant because it will raise
novel legal or policy issues.
Executive Order 13563 reaffirms the principles of Executive Order
12866 while calling for improvements in the Nation's regulatory system
to promote predictability, to reduce uncertainty, and to use the best,
most innovative, and least burdensome tools for achieving regulatory
ends. The Executive Order directs agencies to consider regulatory
approaches that reduce burdens and maintain flexibility and freedom of
choice for the public where these approaches are relevant, feasible,
and consistent with regulatory objectives. E.O. 13563 emphasizes
further that regulations must be based on the best available science
and that the rulemaking process must allow for public participation and
an open exchange of ideas. We have developed this rule in a manner
consistent with these requirements.
Executive Order 13771 (82 FR 9339, Feb. 3, 2017) requires Federal
agencies to take proactive measures to reduce the costs associated with
complying with Federal regulations. Consistent with Executive Order
13771, we have estimated the cost savings for this final rule to be
$14--$34 million per year from the 2015 rule. Therefore, this final
rule is expected to be a deregulatory action under Executive Order
13771.
Regulatory Flexibility Act
The BLM certifies that this rule will not have a significant
economic effect on a substantial number of small entities pursuant to 5
U.S.C. 605(b). The Regulatory Flexibility Act (5 U.S.C. 601 et seq.)
(RFA) generally requires that Federal agencies prepare a regulatory
flexibility analysis for rules subject to the notice and comment
rulemaking requirements under the Administrative Procedure Act (5
U.S.C. 500 et seq.), if the rule would have a significant economic
impact, either detrimental or beneficial, on a substantial number of
small entities (See 5 U.S.C. 601--612). Congress enacted the RFA to
ensure that government regulations do not unnecessarily or
disproportionately burden small entities. Small entities include small
businesses, small governmental jurisdictions, and small not-for-profit
enterprises.
The BLM reviewed the Small Business Administration (SBA) size
standards for small businesses and the number of entities fitting those
size standards as reported by the U.S. Census Bureau in the Economic
Census. The BLM concluded that the vast majority of entities operating
in the relevant sectors are small businesses as defined by the SBA. As
such, the final rule will likely affect a substantial number of small
entities.
Although the final rule will likely affect a substantial number of
small entities, the BLM does not believe that these effects would be
economically significant. This final rule is a deregulatory action that
will remove all of the requirements placed on operators by the 2015
rule. Operators will not have to undertake the compliance activities,
either operational or administrative, that are outlined in the 2015
rule, except to the extent the activities are required by state or
tribal law, or by other pre-existing BLM regulations.
The BLM conducted an economic analysis which estimates that the
average reduction in compliance costs will be a small fraction of a
percent of the profit margin for small companies, which is not a large
enough impact to be considered significant. For more detailed
information, see section 5.3 of the RIA prepared for this final rule.
The final RIA has been posted in the docket for the final rule on the
Federal eRulemaking Portal: https://www.regulations.gov.
Small Business Regulatory Enforcement Fairness Act (SBREFA)
This rule is not a major rule under 5 U.S.C. 804(2), the Small
Business Regulatory Enforcement Fairness Act. This rule will not cause
a major increase in costs or prices for consumers, individual
industries, Federal, state, or local government agencies, or geographic
regions. The rule will not have an annual effect on the economy of $100
million or more.
This rule will not cause a major increase in costs or prices for
consumers, individual industries, Federal, state, or local government
agencies, or geographic regions.
This rule will not have significant adverse effects on competition,
employment, investment, productivity, innovation, or the ability of
U.S.-based enterprises to compete with foreign-based enterprises.
This final rule is a deregulatory action that removes all of the
requirements placed on operators by the 2015 rule. Operators will not
have to undertake the compliance activities, either operational or
administrative, that would have been required solely by the 2015 rule.
The screening analysis conducted by the BLM estimates the average
reduction in compliance costs will be a small fraction of a percent of
the profit margin for companies, which is not large enough to: Have
significant adverse effects on competition, employment, investment,
productivity, innovation, or the ability of U.S.-based enterprises to
compete with foreign-based enterprises; cause a major increase in costs
or prices for consumers, individual industries, Federal, state, or
local government agencies, or geographic regions; or have an annual
effect on the economy of $100 million or more.
Unfunded Mandates Reform Act
This rule does not impose an unfunded mandate on state, local, or
tribal governments, or the private sector of more than $100 million per
year. The rule does not have a significant or unique effect on State,
local, or tribal governments or the private sector. A statement
containing the information required by the Unfunded Mandates Reform Act
(2 U.S.C. 1531 et seq.) (UMRA) is not required. This rule is also not
subject to the requirements of section 203 of UMRA because it contains
no regulatory requirements that might significantly or uniquely affect
small governments, because it contains no requirements that apply to
such
[[Page 61948]]
governments, nor does it impose obligations upon them.
Takings (EO 12630)
This rule does not affect a taking of private property or otherwise
have taking implications under Executive Order 12630. A takings
implication assessment is not required. This rule is a deregulatory
action that removes all of the requirements placed on operators solely
by the 2015 rule and therefore will impact some operational and
administrative requirements on Federal and Indian lands. All such
operations are subject to lease terms which expressly require that
subsequent lease activities be conducted in compliance with
subsequently adopted Federal laws and regulations. This rule conforms
to the terms of those leases and applicable statutes and, as such, the
rule is not a government action capable of interfering with
constitutionally protected property rights. Therefore, the BLM has
determined that the final rule will not cause a taking of private
property or require further discussion of takings implications under
Executive Order 12630.
Federalism (E.O. 13132)
Under the criteria in section 1 of Executive Order 13132, this rule
does not have sufficient federalism implications to warrant the
preparation of a federalism summary impact statement. A federalism
summary impact statement is not required. The final rule will not have
a substantial direct effect on the states, on the relationship between
the Federal Government and the states, or on the distribution of power
and responsibilities among the levels of government. It will not apply
to states or local governments or state or local governmental entities.
The rule will affect the relationship between operators, lessees, and
the BLM, but it does not directly impact the states. Therefore, in
accordance with Executive Order 13132, the BLM has determined that this
final rule does not have sufficient federalism implications to warrant
preparation of a federalism assessment.
Civil Justice Reform (E.O. 12988)
This rule complies with the requirements of Executive Order 12988.
More specifically, this rule meets the criteria of section 3(a), which
requires agencies to review all regulations to eliminate errors and
ambiguity and to write all regulations to minimize litigation. This
rule also meets the criteria of section 3(b)(2), which requires
agencies to write all regulations in clear language with clear legal
standards.
Consultation With Indian tribes (E.O. 13175 and Departmental Policy)
The Department strives to strengthen its government-to-government
relationship with Indian tribes through a commitment to consultation
with Indian tribes and recognition of their right to self-governance
and tribal sovereignty. The BLM has evaluated this final rule in
accordance with the Department's consultation policies and under the
criteria in Executive Order 13175. The BLM authorizes oil and gas
operations that are proposed on Indian onshore oil and gas leases.
Therefore, the rule has the potential to affect Indian tribes and
tribal lands.
Potentially affected tribes were provided an opportunity to provide
feedback and consult with the BLM regarding this rule. The BLM has
fully considered tribal views made known to us in preparing this final
rule.
Paperwork Reduction Act (44 U.S.C. 3501 et seq.)
The Paperwork Reduction Act (PRA) (44 U.S.C. 3501-3521) provides
that 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 control number issued by the Office of Management and
Budget (OMB). Collections of information include requests and
requirements that an individual, partnership, or corporation obtain
information, and report it to a Federal agency. See 44 U.S.C. 3502(3);
5 CFR 1320.3(c) and (k).
This rule rescinds information collection activities that would
have required approval by the OMB under the PRA had the 2015 rule
become effective. OMB pre-approved those activities and assigned
control number 1004-0203 to them, but the control number was not
activated. In view of the rescission, there will be no need to continue
the information collection activities that the OMB has pre-approved
under control number 1004-0203. Accordingly, the BLM will request that
the OMB discontinue that control number after the effective date of
this final rule.
In accordance with this final rule, the BLM will include in its
request for renewal of control number 1004-0137 (expires January 31,
2018) that nonroutine fracturing jobs be removed from the information
collection activity for subsequent well operations, at 43 CFR 3162.3-2.
National Environmental Policy Act
The BLM prepared an environmental assessment (EA) to document its
examination of the potential environmental impacts that may occur as a
result of this final rule. The BLM has determined that this rule does
not constitute a major Federal action significantly affecting the
quality of the human environment. A detailed statement under the
National Environmental Policy Act of 1969 is not required because we
reached a Finding of No Significant Impact (FONSI) for this final rule.
The final EA and FONSI that were prepared for this final rule have
been placed in the file for the BLM's Administrative Record for the
final rule at the BLM's 20 M Street address specified in the ADDRESSES
section. The final EA and FONSI have also been posted in the docket for
the final rule on the Federal eRulemaking Portal: https://www.regulations.gov. The BLM invites the public to review these
documents.
Effects on the Energy Supply (E.O. 13211)
This final rule is not a significant energy action under the
definition in Executive Order 13211. A statement of Energy Effects is
not required. Section 4(b) of Executive Order 13211 defines a
``significant energy action'' as ``any action by an agency (normally
published in the Federal Register) that promulgates or is expected to
lead to the promulgation of a final rule or regulation, including
notices of inquiry, advance notices of rulemaking, and notices of
rulemaking: (1)(i) That is a significant regulatory action under
Executive Order 12866 or any successor order, and (ii) is likely to
have a significant adverse effect on the supply, distribution, or use
of energy; or (2) that is designated by the Administrator of [OIRA] as
a significant energy action.''
Since this final rule is a deregulatory action and would reduce
compliance costs, it is likely to have a positive effect, if any, on
the supply, distribution, or use of energy, and not a significant
adverse effect. As such, we do not consider the final rule to be a
``significant energy action'' as defined in Executive Order 13211.
Authors
The principal author(s) of this rule are Justin Abernathy, Senior
Policy Analyst, BLM, Washington Office; Michael Ford, Economist, BLM,
Washington Office; James Tichenor, Economist, BLM, Washington Office;
Ross Klein, (Acting) Natural Resource Specialist, BLM, Washington
Office; Subijoy Dutta, Lead
[[Page 61949]]
Petroleum Engineer, BLM, Washington Office; Jeffrey Prude, Petroleum
Engineer/Oil and Gas Program Lead, BLM, Bakersfield Field Office; and
James Annable, Petroleum Engineer, BLM, Royal Gorge Field Office;
assisted by Charles Yudson of the BLM's Division of Regulatory Affairs
and by Richard McNeer and Ryan Sklar of the Department of the
Interior's Office of the Solicitor.
Dated: December 22, 2017.
Joseph Balash,
Assistant Secretary--Land and Minerals Management, U.S. Department of
the Interior.
List of Subjects in 43 CFR Part 3160
Administrative practice and procedure, Government contracts,
Indians-lands, Mineral royalties, Oil and gas exploration, Penalties,
Public lands-mineral resources, Reporting and recordkeeping
requirements.
For the reasons stated in the preamble, and under the authorities
stated below, the Bureau of Land Management amends 43 CFR part 3160 as
follows:
PART 3160--ONSHORE OIL AND GAS OPERATIONS
0
1. The authority citation for part 3160 continues to read as follows:
Authority: 25 U.S.C. 396d and 2107; 30 U.S.C. 189, 306, 359,
and 1751; 43 U.S.C. 1732(b), 1733, and 1740; and Sec. 107, Pub. L.
114-74, 129 Stat. 599, unless otherwise noted.
Subpart 3160--Onshore Oil and Gas Operations: General
0
2. Revise Sec. 3160.0-3 to read as follows:
Sec. 3160.0-3 Authority.
The Mineral Leasing Act, as amended and supplemented (30 U.S.C. 181
et seq.), the Act of May 21, 1930 (30 U.S.C. 301-306), the Mineral
Leasing Act for Acquired Lands, as amended (30 U.S.C. 351-359), the Act
of March 3, 1909, as amended (25 U.S.C 396), the Act of May 11, 1938,
as amended (25 U.S.C. 396a-396q), the Act of February 28, 1891, as
amended (25 U.S.C. 397), the Act of May 29, 1924 (25 U.S.C. 398), the
Act of March 3, 1927 (25 U.S.C. 398a-398e), the Act of June 30, 1919,
as amended (25 U.S.C. 399), R.S. Sec. 441 (43 U.S.C. 1457), the
Attorney General's Opinion of April 2, 1941 (40 Op. Atty. Gen. 41), the
Federal Property and Administrative Services Act of 1949, as amended
(40 U.S.C 471 et seq.), the National Environmental Policy Act of 1969,
as amended (40 U.S.C. 4321 et seq.), the Act of December 12, 1980 (94
Stat. 2964), the Combined Hydrocarbon Leasing Act of 1981 (95 Stat.
1070), the Federal Oil and Gas Royalty Management Act of 1982 (30
U.S.C. 1701), the Indian Mineral Development Act of 1982 (25 U.S.C.
2102), and Order Number 3087, dated December 3, 1982, as amended on
February 7, 1983 (48 FR 8983) under which the Secretary consolidated
and transferred the onshore minerals management functions of the
Department, except mineral revenue functions and the responsibility for
leasing of restricted Indian lands, to the Bureau of Land Management.
0
3. Amend Sec. 3160.0-5 by removing the definitions of ``Annulus,''
``Bradenhead,'' ``Cement Evaluation Log (CEL),'' ``Confining zone,''
``Hydraulic fracturing,'' ``Hydraulic fracturing fluid,'' ``Isolating
or to isolate,'' ``Master hydraulic fracturing plan,'' ``Proppant,''
and ``Usable water,'' and by adding the definition of ``Fresh water''
in alphabetical order to read as follows:
Sec. 3160.0-5 Definitions.
* * * * *
Fresh water means water containing not more than 1,000 ppm of total
dissolved solids, provided that such water does not contain
objectionable levels of any constituent that is toxic to animal, plant
or aquatic life, unless otherwise specified in applicable notices or
orders.
* * * * *
Subpart 3162--Requirements for Operating Rights Owners and
Operators
0
4. Amend Sec. 3162.3-2 by revising the first sentence of paragraph (a)
and revising paragraph (b) to read as follows:
Sec. 3162.3-2 Subsequent well operations.
(a) A proposal for further well operations shall be submitted by
the operator on Form 3160-5 for approval by the authorized officer
prior to commencing operations to redrill, deepen, perform casing
repairs, plug-back, alter casing, recomplete in a different interval,
perform water shut off, commingling production between intervals and/or
conversion to injection. * * *
(b) Unless additional surface disturbance is involved and if the
operations conform to the standard of prudent operating practice, prior
approval is not required for routine fracturing or acidizing jobs, or
recompletion in the same interval; however, a subsequent report on
these operations must be filed on Form 3160-5.
* * * * *
0
5. Revise Sec. 3162.3-3 to read as follows:
Sec. 3162.3-3 Other lease operations.
Prior to commencing any operation on the leasehold which will
result in additional surface disturbance, other than those authorized
under Sec. 3162.3-1 or Sec. 3162.3-2, the operator shall submit a
proposal on Form 3160-5 to the authorized officer for approval. The
proposal shall include a surface use plan of operations.
0
6. Amend Sec. 3162.5-2 by revising the heading and first sentence of
paragraph (d) to read as follows:
Sec. 3162.5 -2 Control of wells.
* * * * *
(d) Protection of fresh water and other minerals. The operator
shall isolate freshwater-bearing and other usable water containing
5,000 ppm or less of dissolved solids and other mineral-bearing
formations and protect them from contamination. * * *
[FR Doc. 2017-28211 Filed 12-28-17; 8:45 am]
BILLING CODE 4310-84-P