Topsoil Redistribution and Revegetation Success Standards, 51684-51706 [06-7249]
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Federal Register / Vol. 71, No. 168 / Wednesday, August 30, 2006 / Rules and Regulations
I. Background Information on the
Rulemaking
DEPARTMENT OF THE INTERIOR
Office of Surface Mining Reclamation
and Enforcement
RIN 1029–AC02
30 CFR Parts 816 and 817
Topsoil Redistribution and
Revegetation Success Standards
Office of Surface Mining
Reclamation and Enforcement, Interior.
ACTION: Final rule.
AGENCY:
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SUMMARY: We, the Office of Surface
Mining Reclamation and Enforcement
(OSM), are finalizing minor changes to
our regulations to improve the quality
and diversity of revegetation in the
reclamation of coal mined lands. These
revisions govern topsoil redistribution
and revegetation success standards and
will: Encourage species diversity on
reclaimed lands by allowing
replacement of soil in variable
thicknesses; provide more flexibility to
States in using new vegetative success
standards and sampling techniques by
removing the current requirement that
such changes be included in the
approved regulatory program; define
success standards for lands with an
undeveloped land postmining land use;
remove shelter belts from the list of
postmining land uses subject to success
standards; provide more flexibility to
operators when they demonstrate
compliance with time-in-place
requirements by allowing them to
consider all trees and shrubs in place at
bond release, including volunteer trees
and shrubs, and not requiring them to
verify the length of time that individual
trees and shrubs have been in place—
this change will remove a significant
impediment to reforestation of mined
lands; and make the timing of
revegetation success measurements in
areas receiving 26 inches of annual
precipitation or less consistent with
those in areas receiving more than 26
inches of annual precipitation.
DATES: Effective Date: September 29,
2006.
FOR FURTHER INFORMATION CONTACT:
Robert Postle, Office of Surface Mining
Reclamation and Enforcement, U.S.
Department of the Interior, P.O. Box
46667, Denver, CO 80201; Telephone:
303–844–1400, extension 1469. E-mail:
bpostle@osmre.gov.
SUPPLEMENTARY INFORMATION:
I. Background Information on the
Rulemaking
II. Discussion of the Revisions and Our
Response to the Comments Submitted
III. Procedural Matters and Required
Determinations for This Rule
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Why are we revising our regulations?
On March 17, 2005, we published
proposed revisions to our regulations
that govern portions of the performance
standards dealing with topsoil
redistribution and evaluation of
revegetation success. 70 FR 13076. The
revisions contained in this final rule are
the product of several outreach efforts
by OSM to review and assess its
revegetation regulations at §§ 816.111
through .116 and §§ 817.111 through
.116. The first outreach effort occurred
in 1999. As part of this revegetation
initiative, we published a Federal
Register notice on May 17, 1999 (64 FR
26773), announcing public meetings
and soliciting comments, concerns, and
new ideas regarding the regulatory
performance standards that determine
revegetation success. In the notice, we
also announced the availability of an
OSM concept paper that reviewed
various longstanding revegetation
issues. We held ten public meetings
around the country between May 27 and
August 25, 1999. In the spring of 2003,
as a follow-up to the 1999 revegetation
initiative, we conducted a survey of
State regulatory authorities. This survey
explored whether the statistical and/or
production requirements of the current
revegetation regulations at § 816.116
and § 817.116 adversely affect the
establishment of a diverse plant
community; whether there is a
continuing need for inclusion of success
standards and sampling techniques in a
State’s approved program; and whether
there is a need for success standards for
undeveloped postmining land.
In addition to the revegetation
initiative and survey, we also
established a reforestation outreach
initiative that began with three
workshops held between January 1999
and May 2002 involving Federal and
State regulatory personnel, industry
representatives, and landowners. As
part of this second initiative, we raised
the question whether specific OSM
regulations act as a disincentive to the
choice of forestry as a postmining land
use.
Largely as a result of these
revegetation and reforestation initiatives
and the survey, we identified five minor
revisions that we needed to make to the
existing regulations. This rule revises
the Federal regulations governing the
topsoil redistribution standards at
§ 816.22(d)(1) and § 817.22(d)(1); the
success standards and sampling
techniques requirements at
§ 816.116(a)(1) and § 816.117(a)(1); the
land use categories subject to the
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success standards at § 816.116(b)(3) and
§ 817.116(b)(3); the revegetation success
standards for trees and shrubs at
§ 816.116(b)(3)(ii) and
§ 817.116(b)(3)(ii); and the timing of
revegetation success measurements at
§ 816.116(c)(3)(i) and (ii) and
§ 817.116(c)(3)(i) and (ii).
These revisions will, respectively,
encourage species diversity on
reclaimed lands by allowing
replacement of soil in variable
thicknesses; provide more flexibility to
States in using new vegetative success
standards and sampling techniques by
removing the current requirement that
such changes be included in the
approved regulatory program; define
success standards for lands with an
undeveloped land postmining land use;
remove shelter belts from the list of
postmining land uses subject to success
standards; provide more flexibility to
operators when they demonstrate
compliance with time-in-place
requirements by allowing them to
consider all trees and shrubs in place at
bond release, including volunteer trees
and shrubs, and not requiring them to
verify the length of time that individual
trees and shrubs have been in place—
this change will remove a significant
impediment to reforestation of mined
lands; and make the timing of
revegetation success measurements in
areas receiving 26 inches of annual
precipitation or less consistent with
those in areas receiving more than 26
inches of annual precipitation. Since the
soil redistribution and revegetation
success standards are identical for
surface and underground mining
activities, this preamble will discuss our
revisions to part 816 with the
understanding that the discussion also
applies to our revisions to part 817.
In response to the Federal Register
notice of our 2005 proposed rule, we
received a total of 34 comments. We
discuss the comments and our
responses to those comments below. No
one requested a public hearing.
II. Discussion of the Revisions and Our
Response to the Comments Submitted
1. Section 816.22(d)(1)(i): Topsoil
Redistribution
What are the revisions to
§ 816.22(d)(1)(i)?
In order to improve the potential for
establishing diverse plant communities
consistent with the specific revegetation
goals for an approved postmining land
use, we are adopting, as generally
proposed and further revised in
response to comments received, topsoil
redistribution provisions at
§ 816.22(d)(1)(i) that specify the manner
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in which topsoil material removed
under § 816.22(a) or (b) must be
redistributed. Final § 816.22(d)(1)(i) will
read as follows, with new language in
italics:
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(d) Redistribution. (1) Topsoil materials
and topsoil substitutes and supplements
removed under paragraphs (a) and (b) of this
section shall be redistributed in a manner
that—
(i) Achieves an approximately uniform,
stable thickness when consistent with the
approved postmining land use, contours, and
surface-water drainage systems. Soil
thickness may also be varied to the extent
such variations help meet the specific
revegetation goals identified in the permit;
Under the prior topsoil redistribution
regulations at § 816.22(d)(1)(i), topsoil
must be redistributed in a manner that
‘‘achieves an approximately uniform,
stable thickness consistent with the
approved postmining land use * * *.’’
This requirement that topsoil be
redistributed (or ‘‘replaced’’) to an
approximately uniform thickness has
proven to be particularly appropriate
when the approved postmining land
uses are, for example, commercial
forestry or cropland, both of which may
involve a single species of vegetative
cover in a managed agricultural
environment. However, when the
approved postmining land uses are
wildlife habitat or grazing land that
require satisfaction of specified
vegetative diversity standards for bond
release, the requirement in
§ 816.22(d)(1)(i) that topsoil be replaced
to an approximately uniform thickness
may often work against the achievement
of those vegetative diversity standards.
This is because a plant community that
will sustain itself without constant
management input is, to a considerable
degree, a function of the physical and
chemical characteristics of the soil upon
which it is growing. In turn, variable
topsoil depth is one of the several
physical characteristics that operators
can use to encourage the desired species
diversity.
As discussed in the preamble to the
proposed rule, when we first
promulgated our topsoil regulations
over 20 years ago, we noted that two
commenters had objected to the
proposed uniform thickness
requirement as being a design standard,
not a performance standard. 48 FR
22092, May 16, 1983. These commenters
warned that the rule’s uniform soil
thickness requirement could lead to a
monoculture vegetative community
rather than a diverse native species
community. We did not accept this
comment, responding that topsoil
thickness is but one of several factors
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affecting plant growth and species
diversification.
More recently, in response to our
1999 revegetation outreach effort,
commenters again questioned the
appropriateness of the § 816.22(d)(1)(i)
provision, which they interpreted as
requiring that topsoil always be
redistributed to a uniform thickness.
These commenters stated that uniform
soil thickness tends to promote a
limited number of species in the
vegetative cover while variable soil
thicknesses tend to promote a more
diverse vegetative community. The truth
of this proposition has been born out by
the experience of OSM agronomists and
is consistent with well-established
principles of soil-plant relationships. As
proposed, we have revised our
regulations at § 816.22(d)(1)(i) by adding
a sentence that expressly allows soil
thickness to be varied to the extent such
variations help to meet the specific
revegetation goals identified in the
permit. Also as proposed, we have
inserted the word ‘‘when’’ between the
words ‘‘thickness’’ and ‘‘consistent’’ in
the existing language of § 816.22(d)(1)(i).
This insertion should make clear that
the uniform soil thickness provision is
a function of the approved postmining
land use, contours, and surface water
drainage systems, and is not, in itself, an
inflexible requirement.
While the prior uniform topsoil
redistribution standard of
§ 816.22(d)(1)(i) has generally worked
quite well, the new revisions to that
standard are intended to provide the
operator with another tool for
encouraging the development of the
diverse plant communities required of
specific postmining land uses. For
example, if the designated postmining
land use is fish and wildlife habitat, and
the desired plant communities are a
mixture of grasslands with interspersed
shrub and tree areas for wildlife cover,
then the permit could describe the use
of variable topsoil thickness to ensure
the establishment of grasses on thicker
soils and trees and shrubs on thinner
soils. The fact that the permit applicant
must clearly set forth the justification
for any non-uniform redistribution of
topsoil should largely protect against
potential abuse. This revised rule will
not affect existing topsoil salvage
requirements.
In response to comments, we have
further revised § 816.22(d)(1) to provide
that topsoil materials and topsoil
substitutes and supplements removed
under paragraphs (a) and (b) must be
redistributed in a manner that meets the
requirements of subparagraphs (i)-(iii).
(Emphasis added). This last revision
should make clear that, under
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appropriate circumstances, the variable
thickness revision of § 816.116(d)(1)(i)
applies to topsoil supplements and
substitutes already allowed under
§ 816.22(a) and (b).
What were the comments submitted on
our proposed revisions to
§ 816.22(d)(1)(i)?
Seventeen commenters supported our
proposed revision to the topsoil
redistribution requirements of
§ 816.22(d)(1)(i). Their comments
focused on the potential to be gained
from varying topsoil thickness in
establishing diverse plant communities.
The commenters noted that research
supports our contention that topsoil
thickness affects the types, number, and
densities of plants established in a
particular area. These commenters also
generally supported our position that
the use of variable topsoil thickness to
meet specific revegetation goals
identified in the permit will assist
operators in establishing more diverse
plant communities on areas where such
diversity is appropriate to meet the
postmining land use.
Four commenters proposed an
additional revision to § 816.22(d)(1).
They suggested that we further amend
§ 816.22(d)(1) to apply to topsoil and
topsoil supplements and substitutes
removed under paragraphs § 816.22 (a)
and (b) of this section. The commenters
indicated that the revision that we
proposed inappropriately applies only
to topsoil materials as defined at
§ 701.5, which states that ‘‘[t]opsoil
means the A and E soil horizon layers
of the four master soil horizons.’’ The
commenters saw this as a problem
because western coal mines are often
located in areas where the native soils
are poorly developed. At many of these
mines, the A and E horizons are absent
or insufficient in thickness to provide
sufficient material for reclamation.
Consequently, to meet their reclamation
goals, operators must rely on the use of
suitable unconsolidated materials
immediately below the topsoil and on
the use of selected overburden as topsoil
supplements and/or substitutes. The
commenters further noted that in other
situations operators use very specific
topsoil substitutes to establish specific
or unique plant communities. For
example, ongoing revegetation efforts
have shown that substitute materials
with high rock fragment content are best
for reestablishing woody species in
parts of the West. Accordingly, the
commenters argued that we needed to
broaden our proposed revision to
§ 816.22(d)(1) to expressly allow for
removed material, be it topsoil, topsoil
supplements, or topsoil substitutes, to
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be replaced in variable thicknesses to
meet specific revegetation goals.
According to commenters this change
would allow western surface coal mine
operators to share in the benefits that
our proposed rule was intended to
achieve.
We believe that these commenters
have raised a valid concern about the
applicability of § 816.22(d)(1) to the
replacement of topsoil supplements or
to substitutes currently allowed under
§ 816.22(b). Many approved reclamation
plans throughout the country already
allow the use of topsoil supplements or
substitutes. Regulatory authorities often
permit use of such supplements or
substitutes where there is insufficient
topsoil, defined as A and E horizon
material, to ensure the prescribed
revegetation success. In other cases,
they have approved topsoil substitutes
when applicants have demonstrated that
the existing topsoil is less suitable as
plant growth material for the desired
plant community than available subsoil
or spoil material. For many years we
have interpreted § 816.22(d)(1) as
applying to both topsoil material
removed under § 816.22(a) and to
topsoil supplements or substitutes
removed under § 816.22(b). Pursuant to
this interpretation, once operators
identify and remove approved topsoil
supplements or substitutes, they may
treat this material as topsoil material for
the purposes of storage and
redistribution. However, to eliminate
any potential confusion as to whether,
under appropriate circumstances, the
variable thickness revision of
§ 816.22(d)(1)(i) applies to topsoil
supplements and substitutes already
allowed under § 816.22(a) and (b), we
are accepting the comment and revising
§ 816.22(d)(1) as the commenters
suggested. Accordingly, as set forth
above, final § 816.22(d)(1) will provide
that ‘‘(1) Topsoil materials and topsoil
substitutes and supplements removed
under paragraphs (a) and (b) of this
section shall be redistributed in a
manner that—’’ (Emphasis added).
Hereafter, references to variable topsoil
replacement also includes variable
replacement of topsoil substitutes and
supplements.
Two commenters suggested
eliminating from § 816.22 (a) the
requirement to remove, i.e., salvage all
topsoil. These commenters contend that,
based on our proposal to allow
replacement of topsoil at variable
depths, we should be flexible and, at
least in certain circumstances, also
allow operators not to remove and
replace all ‘‘available’’ topsoil. They
argued that to require removal of all
available topsoil would potentially
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defeat the purpose in the proposed rule
of allowing shallower topsoil depths. In
addition, the commenters pointed out
that, according to mine reclamation
professionals, shallower topsoil depths
increase plant community diversity and
woody stem density, while deeper than
average topsoil depths (that would
compensate for the areas where topsoil
is applied more shallowly than the
uniform average) only encourage
aggressive grass and forb species at the
expense of diversity and woody stem
density.
While the commenters are correct that
shallower soils can increase plant
diversity and woody stem density, we
are not revising the regulations as they
proposed. The existing regulations at
§ 816.22(a) will continue to require the
removal of all topsoil, defined
elsewhere as A and E horizon material.
For several reasons we do not believe
that these regulations pose the problem
suggested by the commenters. Most
importantly, section 515(b)(5) of the
Surface Mining Control and
Reclamation Act of 1977 (SMCRA or the
Act), clearly requires the removal and
replacement of all suitable topsoil.
Furthermore, natural landscapes usually
include areas with deep soils as well as
shallower soils. This in turn results in
multiple distinct plant communities
across the landscape. When we require
uniform soil thickness for reclamation,
the result may be a single plant
community but little plant community
variability across the landscape.
Conversely, when we require
reclamation that includes areas with
deep soils as well as shallower soils, the
result is more likely the establishment
of multiple diverse plant communities,
including those that prefer deeper soils
as well as those that prefer shallower
soils. The purpose of the rule is not, as
commenters characterize, to allow for
shallower topsoil depths throughout the
reclamation area. Instead, the rule
requires removal of all topsoil to allow
development of reclamation and
revegetation plans that can maximize
the use of that topsoil through the
placement of variable topsoil depths
and the reconstruction of a much more
diverse landscape similar to that which
may have existed prior to mining.
One commenter indicated that, if we
allow variation in soil thickness
(specifically reductions in soil
thickness), we must also require the
operator to demonstrate that an equal or
greater chance for sustaining vegetation
success will result. In addition, the
commenter stated that the operator
should have to demonstrate that the
reconstructed soil has a root zone of
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sufficient depth to support the approved
postmining land use.
We generally agree with this comment
but do not believe that any change in
the revised regulation is necessary to
ensure the desired variation of soil
thickness. The revised language of
§ 816.22(d)(1)(i) allows operators to vary
soil thickness to the extent necessary to
meet the specific revegetation goals
identified in the permit. In turn, these
revegetation goals should support the
approved postmining land use. The
State and the public will have the
opportunity to review the permit prior
to approval and determine whether the
permittee has justified the need for
variable topsoil thicknesses in order to
achieve the identified revegetation
goals. If the permittee has failed to do
so, the State can disapprove the use of
variable topsoil thicknesses or require
additional information to justify
departure from the normal practice. On
this basis, we do not believe that the
demonstration proposed by the
commenter is necessary.
One commenter opposed our
proposed revision to the topsoil
redistribution requirements of
§ 816.22(d)(1)(i). Instead of replacing all
the soil that was lost to strip-mining, the
commenter alleged that, under revised
§ 816.116(d)(1)(i), coal companies could
replace only some of the removed soil.
The commenter opposed the change to
§ 816.22(d)(1)(i) because, according to
him, it could ‘‘let coal companies do
even less to bring the land they’ve
mined back to its original condition.’’
This commenter seems to have
misunderstood our proposal. It does not
scrap the current standard. As before,
the revised regulation will require
operators to remove all topsoil from
areas that are to be disturbed by mining.
After mining, they must redistribute all
removed topsoil on areas disturbed by
mining. The proposed and final rules
merely allow operators whose
reclamation plan and postmining land
use require the establishment of diverse
plant communities as part of specific
revegetation goals identified in the
permit to redistribute topsoil at variable
thicknesses rather than at approximate
uniform thickness. For the reasons
stated above, we believe that the
revision to § 816.22(d)(1)(i) will result in
improved and more diverse reclamation.
Another commenter observed that the
proposed revision to § 816.22(d)(1)(i)
will require better planning on the part
of companies at the permitting stage,
and that they must complete all
vegetation planning prior to completion
of rough grading and prior to topsoil
replacement. The commenter, however,
expressed concern that those who
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thought that the proposal would make
reforestation more successful may be
disappointed.
We strongly agree that allowing
variable topsoil thickness under the new
provisions of § 816.22(d)(1)(i) will
require appropriate planning by
operators. As expressly stated in final
§ 816.22(d)(1)(i), operators can vary soil
thickness only if they justify this
variation based on specific revegetation
goals identified in the permit. The
permit would necessarily have to
include a discussion of plans for
variable topsoil thickness. Furthermore,
an approved permit would have to be in
place prior to implementation of any
plan for regrading, topsoil
redistribution, or revegetation. While
there can be no guarantee as to how
much the revision to § 816.22(d)(1)(i)
will actually increase reforestation of
reclaimed areas, we reasonably believe
that the revision should encourage
reforestation and species diversity.
Another commenter suggested that we
should broaden the proposed revision to
§ 816.22(d)(1)(i) to allow variable
replacement thicknesses for (1) suitable
unconsolidated materials located
immediately below the topsoil, and (2)
selected overburden used as topsoil
supplements and/or substitutes when
the use of such materials would help to
meet the reclamation goals identified in
the permit. In the course of its own
reclamation activities this commenter
had found that selected overburden
materials, including scoria of suitable
fragment size range, are vitally
important to creating diverse vegetation
types such as open scrub, and highly
conducive to establishing several shrub
species in the genus Artemisia.
With regard to the commenter’s first
suggestion, we note that § 816.102(f)
already addresses the thickness of the
suitable unconsolidated material that is
replaced below the topsoil. The
regulation expressly requires that
exposed coal seams, acid- and toxicforming materials, and combustible
materials exposed, used, or produced
during mining must either be
adequately covered with nontoxic and
noncombustible material, or treated, to
control the impact of the materials on
surface and ground water in accordance
with § 816.41, to prevent sustained
combustion, and to minimize adverse
effects on plant growth and the
approved postmining land use. Section
816.102(f) does not specify the thickness
of the layer of nontoxic material that
must cover acid- and toxic-forming
materials. The regulation thus permits
variable redistribution thicknesses of
suitable unconsolidated material that is
found below the topsoil. As to the
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commenter’s second proposal, we have
already stated that § 816.22(d)(1)(i)
properly applies to topsoil supplements
and substitutes and have revised the
regulation to clarify this point.
Accordingly, final § 816.22(d)(1) will
apply to both topsoil removed under
§ 816.22(a) and topsoil supplements and
substitutes used in accordance with
§ 816.22(b).
Another commenter indicated that the
proposed revision to § 816.22(d)(1)(i)
allowing for variable soil thickness was
unnecessary for achievement of our
stated purpose of encouraging greater
plant diversity. This commenter
asserted that the existing rules afford
operators the flexibility to vary soil
thicknesses in appropriate cases. The
commenter stated that reclamation
plans within a single permit area can be,
and have been designed to
accommodate the needs of croplands,
grasslands, and woodland plants by
varying soil thicknesses in the areas
where each vegetation type will be
planted. According to the commenter,
several other factors have far more
influence upon the diversity of the postmining vegetative communities than do
variable soil thicknesses. These factors
include the particular vegetation that is
to be planted after mining, the quality
of the soil replaced, and the degree to
which soil compaction is prevented.
The commenter continued that the
current regulation at § 816.22(d)(1)(i)
requiring the replacement of an
approximately uniform thickness of
topsoil provides for the protection, use,
and productivity of soil resources in a
way that should restore the capability of
the land to support a wide variety of
vegetation types and land uses. In
support of our retaining the
longstanding provisions of
§ 816.22(d)(1), the commenter
emphasized that the segregation and
replacement of topsoil over entire
reclaimed areas has been successful
over the fifty-seven years of regulating
the restoration of mined lands. This
commenter further noted that the
proposed revision to § 816.22(d)(1)(i)
would not provide minimum thickness
requirements for topsoil redistribution.
The commenter cautioned that, while
variable topsoil thickness may improve
attainment of certain land use types, too
thin a layer of topsoil could prove
counterproductive to the attainment of
ground cover, erosion protection, water
quality protection, and restoration of
productive capability of the land. The
commenter concluded, therefore, that
any provision allowing replacement of
variable topsoil or topsoil-substitute
thicknesses should also provide for a
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minimum topsoil or soil-substitute
thickness. This commenter also
indicated that his experience is not
consistent with the statement in our
preamble that ‘‘[t]he fact that a permit
applicant must clearly set forth the
justification for any non-uniform
redistribution of topsoil should largely
protect against potential abuse.’’
According to the commenter, it would
be easier for a regulatory authority to
sustain challenges to a finding of noncompliance with a specific performance
standard, e.g., that operators must
redistribute topsoil in an uniform
thickness, than to sustain challenges to
a finding that the operator has not
adequately set forth the justification for
non-uniform thicknesses.
We disagree with these comments and
concerns. Most importantly, we do not
consider that the revision to
§ 816.116(d)(1)(i) represents a reduction
of the regulatory standards. As
discussed in the preamble to our
proposed rule and as reflected in the
express language of that rule, we intend
to allow variable topsoil thicknesses
when necessary to further the specific
revegetation goals identified in the
permit. The fact that the permit
application must clearly set forth the
justification for variable topsoil
thicknesses reasonably protects against
potential abuse. If the regulatory
authority finds that redistribution of
topsoil in variable thicknesses is not
necessary to meet the specific
revegetation goals identified in the
permit application, then the authority
need not approve that aspect of the
application. If, however, the regulatory
authority finds that variable topsoil
thicknesses is desirable, the permit
application should specify the amount
of variability allowable and the
minimum acceptable topsoil thickness.
Contrary to the commenter’s experience,
research in the West on the impact of
topsoil depth on plant diversity has
shown that plant diversity can be
improved with redistribution of variable
topsoil thicknesses. Long-Term Plant
Community Development In Response
to Topsoil Replacement Depth On
Mined Land In Wyoming, C.K. Bowen,
G. Schuman, and R.A. Olson, American
Society of Mining and Reclamation,
2005. Long-Term Effects of Cover Soil
Depth On Plant Community
Development for Reclaimed Mined
Lands in New Mexico, B. Buchanan, M.
Owens, J. Mexal, T. Ramsey, and B.
Musslewhite, American Society of
Mining and Reclamation, 2005.
The same commenter also expressed
concern both about the effect that
proposed § 816.22(d)(1)(i) would have
on the restoration of premine land
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capability and the negative effect that
the revised regulation would have on
one of the basic missions of SMCRAassuring that required reclamation
accounts for the capability of the land
prior to any mining to support a variety
of uses. Simply stated, the commenter
urged us not to stress vegetation
diversity at the expense of the
underlying land capabilities. The
commenter also indicated that, in those
areas of the country where valuable
topsoil resources exist, regulatory
authorities must take into account soil
rooting zone reconstruction for the
proper utilization of those soil
resources. This reconstruction should be
done in a way that would provide not
only for tree productivity but also for
use of the soil resources in a manner
that would maximize the post-mining
capability of the land. Furthermore, the
commenter stated that it is not
necessary to relocate, modify
distribution, or eliminate topsoil
resources in order to ‘‘encourage’’
reforestation as a postmining land use.
The commenter concluded by
characterizing our stated basis for
revising § 816.22(d)(1)(i) as ignoring
‘‘the essential nature and role of topsoil
resources in land use capability and
suitability to support a variety of uses.’’
We agree with the commenter that
topsoil resources must be protected. The
regulations at § 816.22(a) and (d)
continue to require that all topsoil must
be removed and that all removed topsoil
must be redistributed. The revised
regulation at § 816.22(d)(1)(i) simply
provides the opportunity to allow
redistribution of topsoil at variable
thickness when such redistribution is
appropriate to meet the revegetation
goals identified in the permit’s
approved postmining land use plan.
Under the existing regulations in
§ 816.22(e), a regulatory authority can
also require removal and redistribution
of subsoil, if necessary, to comply with
the revegetation requirement of the
regulations. The proposed and final
rules do not, therefore, ignore or negate
the existing land use provisions of
§ 816.133(a), which require that all
disturbed areas be restored in a timely
manner to conditions that are capable of
supporting the uses they were capable
of supporting before mining, or higher
or better uses. Under these rules, if the
regulatory authority determines that the
proposed redistribution of topsoil in
varying thicknesses would adversely
affect the restoration of the land use
capability of an area, then the regulatory
authority need not sanction such
redistribution.
Another commenter noted that the
revised regulation, which allows soil
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thickness to be varied to the extent that
such variation encourages the specific
revegetation goals identified in the
permit, needs to include a modification
and verification provision that would
assure that variation is not a post hoc
effort by the operator to avoid proper
redistribution of topsoil. The
commenter also stated that the rule
must clarify that operators may not vary
topsoil and subsoil redistribution in
those instances where removal and
reconstruction of soils is necessary to
restore mined farmland. The commenter
next argued that the rule’s standard for
justifying variation in topsoil
replacement thickness should be more
precise and measurable than merely
providing that the variation ‘‘help meet’’
the specific revegetation goals identified
in the permit. In this regard, the
commenter stated that the permit
should define the amount of variability
in topsoil thickness and the chemical
quality of the topsoil necessary to meet
identified revegetation goals. Where
uniform thickness is not to be the
standard, the topsoil and subsoil
redistribution plan should also provide
appropriate literature citations
supporting the proposition that the
variation of soil thicknesses is
consistent with, and necessary for, the
success of particular species. Finally,
this commenter asserted that, regardless
of whether the soil thickness is intended
to be relatively uniform or varied to
support a particular species or mixture
of vegetative cover on the reclaimed
land, the State regulatory authority or
OSM, acting under a Federal Program,
should require the operator to
demonstrate compliance with the soil
redistribution requirements of
§ 816.22(d)(1)(i). Furthermore, the State
regulatory authority or OSM should take
sufficient soil thickness measurements
to support a finding of compliance.
We believe that the current and
revised regulations at § 816.22(d)(1)(i)
adequately address the concerns
underlying these comments. The new
provisions of § 816.22(d)(1)(i) that soil
thickness may be varied to the extent
that such variations help meet the
specific revegetation goals identified in
the permit clearly implies the need for
the operator to document how topsoil
will be redistributed prior to such
redistribution. This necessary
documentation should ensure that the
redistribution of topsoil at varied
thicknesses is not a post hoc effort to
avoid proper redistribution. For
example, if the approved postmining
land use is cropland, then redistribution
of topsoil at varied thicknesses would
not be appropriate and operators should
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redistribute the topsoil in an
approximately uniform thickness as is
presently required. However, if the
approved revegetation goals would best
be met by varying topsoil thicknesses,
then the operator must propose and the
regulatory authority must approve these
variations. While we believe that
authoritative literature and/or test plots
are appropriate sources of information
for setting sideboards on the variation in
topsoil thickness, we leave to the
discretion of the regulatory authority
whether to require inclusion of such
literature or test plot data in the permit.
Evaluation of the thickness of
redistributed topsoil based on permit
specifications can be done either as part
of the ongoing inspection process or
based on data submitted by the operator.
In this regard, we anticipate that the
regulatory authority will evaluate the
redistribution of topsoil in varying
thickness in the same manner that it
currently evaluates the redistribution of
topsoil in an approximately uniform
thickness under prior § 816.22(d)(1)(i).
2. Section 816.116(a)(1): Federal
Approval of Revegetation Success
Standards
What are the revisions to
§ 816.116(a)(1)?
We have revised § 816.116(a)(1) to
eliminate the requirement that
revegetation success standards and
statistically valid sampling techniques
be included in the approved regulatory
program (hereinafter ‘‘the approved
program requirement’’). The revised
regulation continues to require that
standards for success and sampling
techniques for measuring success must
be selected by the regulatory authority.
Our proposed elimination of the
approved program requirement was
described in our 2005 Federal Register
notice. As a result of comments received
and discussed below, we are also adding
a provision to § 816.116(a)(1) to clarify
that the standards and techniques
selected by the regulatory authority
shall be described in writing and made
available to the public. Later in this
document we describe several
acceptable means for making the
standards and techniques available to
the public. Final § 816.116(a)(1) will
read as follows, with new language in
italics:
(1) Standards for success and statistically
valid sampling techniques for measuring
success shall be selected by the regulatory
authority, described in writing, and made
available to the public.
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Why are we changing our policy
regarding review of State Program
changes in success standards and
sampling techniques?
As explained in more detail below,
the requirement that State regulatory
authorities include the initial or
amended success standards and
sampling techniques for revegetation as
part of their approved program imposes
a significant and unnecessary burden
both on State regulatory authorities and
OSM. Our regulations at § 816.116(a)(2)
and (b), which will remain in effect,
already specify minimum criteria for
success standards and sampling
techniques, and those criteria will
ensure the achievement of SMCRA’s
goal of establishing a diverse,
permanent, and effective vegetative
cover. Section 816.116(a)(2) provides
that the sampling techniques must use
a 90-percent confidence interval (also
known as a one-sided test with a 0.10
alpha error), which was discussed in the
preamble to the proposed rule, and that
the ground cover, production, or
stocking must meet 90-percent of the
success standard. Section 816.116(b)
provides additional guidelines for
particular types of ecosystems and postmining land uses. These key nationwide
minimum protections will remain in the
regulations as amended, and all
approved State programs must maintain
counterparts to them.
In our judgment, it is not a good use
of State and Federal resources to
continue requiring State and OSM
revegetation experts to spend valuable
time on preparing or assessing new
State program amendment proposals
every time it is necessary to revise or
improve revegetation success standards.
A number of considerations support this
conclusion. First, the amount of time
and resources required to go through the
State program amendment process is
significant and we think discourages
updating the success standards and
sampling techniques. Our processing of
program amendments takes an average
of about four and a half months, ranging
from two and a half to seven months,
but one recent amendment took twenty
months from proposal to final approval.
The time and resources spent on the
program amendment process, moreover,
are in addition to those the States must
devote to preparing proposed program
amendments and to responding to any
of our inquiries. Although we lack
complete data on how great a burden
this regulatory requirement imposes on
the States, the example of North Dakota,
which follows, shows that the
cumulative costs in time and talent can
be quite large. The present component
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of the North Dakota State program for
revegetation success standards and
sampling techniques is now more than
100 pages long. North Dakota has
repeatedly had to submit proposed
amendments for our approval not only
for substantive changes in standards but
even for minor wording changes, such
as the change in the name of a U.S.
Department of Agriculture bureau from
the ‘‘Soil Conservation Service’’ to the
‘‘Natural Resources Conservation
Service.’’ On this basis alone, we think
that the current requirement may well
be discouraging State regulatory
authorities from developing or
implementing the latest, most
appropriate science and technologies.
70 FR 13076, March 17, 2005. This
apparent obstacle to the timely
development of new science and
technologies also runs counter to one of
the main concerns behind our 1983
rulemaking: That the States needed
significant flexibility to tailor standards
and sampling techniques to local
conditions. See 47 FR 40140, September
2. We continue to want to encourage
responsible innovation in this area. As
we mentioned in the preamble to our
2005 proposed rule, we have been
working with western States to develop
new success standard resources,
innovative statistical tools, and
techniques using computers and
satellite-based remote sensing
technologies to better evaluate
conditions of vegetative diversity and
cover than is possible using traditional
sampling methods, particularly in
locations with naturally sparse
vegetation. In the Appalachian Region,
our agency is working with scholars and
the State of West Virginia on the use of
the plate method for evaluating
herbaceous productivity on reclaimed
lands. We believe that removal of the
requirement in § 816.116(a)(1) for
including these standards and
techniques in the approved program
will eliminate an unnecessary obstacle
to appropriate and timely technological
innovation.
Second, we recognize that, since the
basic framework of the existing rule was
first promulgated in 1983, the vast
majority of State regulatory programs
have matured. Our experience with the
State regulatory authorities over the
years has shown that they now have
sufficient expertise to devise or modify
their success standards and sampling
techniques to incorporate new
scientific, technological, or other
information in a manner that assures
proper revegetation of disturbed areas.
In most instances, we have not had to
engage in substantial re-writing of
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51689
changes to State revegetation success
standards or sampling techniques
during the Federal approval process.
However, even though we will no longer
be approving State program
amendments on those issues, our
revegetation experts will remain
available to consult with the State
regulatory authorities on issues
including success standards and
sampling techniques. Thus, our agency
is not withdrawing resources that have
been beneficial to the States as they
pursue SMCRA’s goal of successful
revegetation.
Third, and perhaps most importantly,
the removal of the approved program
requirement from § 816.116(a)(1) leaves
no regulatory void. As previously noted,
the nationwide minimum requirements
for revegetation success and sampling
techniques will continue to apply to the
State regulatory authorities and
indirectly to the permits that those
regulatory authorities issue. Thus, the
revision to § 816.116(a)(1) will not cause
greater divergence among the States that
are already required to meet the
minimum nationwide requirements of
§ 816.116(a)(2) and (b). Even in those
States that by State law are not allowed
to be more stringent than OSM’s
regulations, the minimum nationwide
requirements of § 816.116(a)(2) and (b)
continue to apply. While complying
with those nationwide requirements, the
State regulatory authorities will, under
revised § 816.116(a)(1), also be able to
respond to new or localized scientific,
technical, and land use information in
a timelier manner, without awaiting the
formal process of OSM approval.
Furthermore, there are avenues besides
our approval of success standards and
sampling techniques by which the
public and we may assure compliance
by the State regulatory authorities with
nationwide revegetation requirements.
The success standards and sampling
techniques will have to be included in
each permit issued by the State
regulatory authorities. Thus, contrary to
the assertions of one commenter, the
removal of this requirement will not
lead to compromises in the effective
implementation of SMCRA’s goal of
proper revegetation. In addition, ‘‘any
person with an interest which is or may
be adversely affected may request a
hearing’’ on any permit issued by a State
regulatory authority. § 775.11(a). When
a permittee applies for final bond
release, the surface owner must be
notified and given an opportunity to
participate in the bond-release
inspection. § 800.40(b)(1). Before final
bond release, any person with a valid
legal interest may file objections and
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request a public hearing. § 800.40(f).
The State’s regulatory program must
also provide for administrative hearings
and judicial review. §§ 775.12(b) and
775.13(b). In addition, if, in conducting
an oversight inspection, we were to find
a surface coal mining operation in
violation of the nationwide minimum
requirements, we would take
appropriate action. See § 842.11(a)(1),
(b)(1)(iii)(A). If the State appears to be
including success standards and
sampling techniques in its permits that
are not in compliance with the
nationwide minimum requirements of
§ 816.116(a)(2) and (b), we can initiate
proceedings that could ultimately lead
to substitution of direct Federal
enforcement of the revegetation
requirements, or withdrawal of the
Secretary’s approval of the State
program in whole or in part. § 733.12(a),
(g). Thus, the public’s interest in proper
revegetation remains protected, and the
State regulatory authorities have
incentive to keep their success
standards and sampling techniques in
compliance with the nationwide
minimum requirements that have
applied since 1983.
A final reason for removing the
requirement that revegetation success
standards and sampling techniques be
included in the approved program is
that this requirement is inconsistent
with the approach we have taken in
other areas. States do not have to
include in their approved programs all
of the specific techniques and standards
they use to assess whether other
SMCRA requirements have been met.
See § 780.22 (requiring submission of
the geologic data and overburden
characteristics), § 780.21(d) (requiring
assessment of the probable hydrologic
consequences of mining), and
§ 780.21(g) (requiring a cumulative
hydrologic impact assessment showing,
inter alia, that the operation has been
designed to prevent material damage to
the hydrologic balance outside the
permit area but not defining the term
‘‘material damage’’). Instead, the
regulatory authorities, both States and
OSM, have effectively addressed the
standards to be used in these
determinations or submissions by
developing guidance documents that are
not required to be in the approved
regulatory programs. Moreover, we do
not impose the requirement to
promulgate success standards and
sampling techniques upon ourselves
when we act as a regulatory authority.
None of the three Federal programs with
active mining include specific
vegetation sampling techniques. The
Federal program for the State of
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Washington and the Federal program for
Indian lands do not include specific
revegetation success standards; the only
Federal program with active mining that
includes such requirements is the
regulatory program for Tennessee.
§§ 942.816(f) and 942.817(e). We have
no compelling justification for
continuing such an inconsistent
approach, particularly since there is no
reason to believe that the different
requirements of State and Federal
programs have resulted in significant
divergence of the actual success
standards or sampling techniques in
use, or in the actual success of
revegetation on mined sites. There is
thus no principled reason to believe that
the States cannot effectively implement
revegetation success standards and
sampling techniques without having to
go through the formal promulgation
process imposed by the prior approved
program requirement of § 816.116(a)(1).
What were the comments submitted on
our proposed revisions to
§ 816.116(a)(1)?
In response to our proposed rule, we
received comments from 16 commenters
supporting removal of the approved
program requirement from
§ 816.116(a)(1). Of the 16 commenters,
five were State regulatory authorities,
one was a State coal association, six
were coal companies, and four were
industry associations. In general, these
commenters based their support on the
reduced regulatory burden they affirmed
would result from eliminating the (a)(1)
requirement. They also stated that the
proposal would result in increased
flexibility and improve their ability to
make use of potential new technologies
that may become available. Specific
comments stated that the current
process provides little incentive to
continue or expand research into new
and innovative methods, often results in
unnecessary delays in State
implementation of changes to these
policies that are based on a State’s
professional judgment, and flies in the
face of State primacy. These
commenters stated that the revised
regulation will better enable States to
stay abreast of technological advances
and to tailor success standards to local
conditions, will allow use of alternative
parameters for revegetation success,
such as measurement of a site index,
without submitting program
amendments. Furthermore, the revised
regulations will still support strict
revegetation standards while allowing
States to respond to improvements in
sampling methodologies and
technological advances.
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We agree with these commenters and
are proceeding with the rulemaking as
proposed. The revised regulation will
give the States the flexibility they need
to implement new technologies without
having to go through the Federal
rulemaking process of amending their
approved programs. As discussed above,
we are also adding a provision to
§ 816.116(a)(1) to clarify that the
standards and techniques selected by
the regulatory authority must be
described in writing and made available
to the public. This last provision will
ensure that all interested parties can
readily find out all the options available
in their jurisdiction for evaluating
revegetation success.
Four of the commenters that
supported the proposed revision to
§ 816.116(a)(1) noted that the revision,
and the regulation as a whole, does not
reflect that standards of success and
statistically valid sampling techniques
for measuring success are actually
developed jointly by the permit
applicant and regulatory authority and
incorporated as part of the reclamation
plan approved as part of the permit.
These commenters indicated that
normally the operator proposes such
standards and sampling techniques
prior to conducting baseline vegetation
studies. The commenters agreed that
this is appropriate, as the operator is
most familiar both with the plant
communities that will be affected by the
operation and with the sampling
methods needed to accurately describe
and measure these plant communities.
The commenters indicated that the
standards and sampling techniques will
become subject to evaluation in the
permitting process and will be
ultimately codified in the permit or
letters of concurrence from regulatory
authorities. The commenters further
noted that through this process
sampling methods and success
standards are not ‘‘selected’’ unilaterally
by the regulatory authority.
Accordingly, the commenters suggested
that preamble language of the
§ 816.116(a)(1) revision be improved by
emphasizing the current process by
which a number of the State regulatory
authorities and their permittees jointly
develop success standards and sampling
techniques.
We are retaining the current
requirement of § 816.116(a)(1) that the
regulatory authority select revegetation
success standards and statistically valid
sampling techniques. The selected
success standards and sampling
techniques will be put in writing and be
available to the public and, as before,
will be used by operators in developing
their permit applications. The manner
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in which a regulatory authority goes
about selecting the success standards
and statistically valid sampling
techniques that it will allow operators to
use in evaluating revegetation success is
up to the regulatory authority. That
authority can, as suggested by the
commenters, select the success
standards and sampling techniques in
consultation with operators and/or with
assistance from academia. However,
selected success standards and sampling
techniques must meet the requirements
of § 816.116(a)(2) and (b) and they must
be put in writing and made available to
the public. It is from these identified
success standards and sampling
techniques that the operators must
choose the specific standards and
techniques included in their individual
permit applications. This procedure will
ensure no less consistent revegetation
success evaluations than that afforded
under the prior rule.
We received comments from five
commenters opposed to the proposed
revision deleting the approved program
requirement from § 816.116(a)(1). A
large percentage of these comments
focused on the absence of any provision
in the proposed rule that would provide
for public review of the success
standards and sampling techniques
selected by the regulatory authority.
More specifically, these comments
raised concerns about loss of public
review; lack of enforceable success
standards; inability of the public to
review permits if the success standards
and sampling techniques are not part of
the approved program; and potential
conflict among States, operators, and
landowners over acceptable standards
and sampling techniques. Other
commenter concerns focused on the
lack of support for changing a regulation
that had been in place since 1983 and
the inability of Federal oversight to
prevent problems. These commenters
also stated that the burden of OSM’s
lengthy timeframes for processing State
amendments is self-imposed, that
flexibility already exists within the
Federal regulations for States to develop
success standards and sampling
techniques to fit local conditions, that
inconsistent application of success
standards and sampling techniques will
occur, and that the current process does
not stifle evaluation or utilization of
new technologies. The specific
comments received and our responses
are discussed below.
All five of the commenters opposing
removal of the approved program
requirement from § 816.116(a)(1)
expressed concern with the loss of
public review of selected success
standards and statistically valid
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sampling techniques if the standards
and techniques were no longer included
in the State approved program. These
commenters declared that the removal
of success standards and sampling
techniques from the State approved
programs would result in information
not being available to the public. One of
the commenters asserted that OSM, by
adopting this change, was taking the
attitude that the only parties at interest
in these matters were the companies
and the States. This commenter claimed
that success standards for reclamation
are an extremely important source of
public information and that, under the
proposed rule, it would be more
difficult for the public to find the
success standards approved for a given
permit. The commenter indicated that
the inclusion of important matters in
‘‘internal guidance documents’’ and
‘‘technical standards’’ alone is not
satisfactory. The commenter further
questioned how, under the proposed
rule, the public would know if there
was any internal consistency within and
between States as to selected success
standards or sampling techniques.
Finally, the commenter asserted that
under the proposed rule, as under the
provisions for public review during
permitting at § 773.6(a) and (b)(2), and
as under the provisions for public
involvement in bond release at
§ 800.40(b)(1) and (f), OSM and the
States seemingly want the public to find
the problems that OSM and the States
have missed. The commenter concluded
that it would be hard for the public to
find these problems if the success
standards and sampling techniques are
not in the State regulations.
Two of these commenters further
noted that removal of the approved
program requirement from
§ 816.116(a)(1) eliminates the ability of
the public to comment on the success
standards and sampling techniques
proposed by the States for inclusion in
their approved programs.
In partial response to these
commenters’ concerns, we are adding
the express requirement in final
§ 816.116(a)(1) that the standards and
techniques selected by the States be in
writing and made available to the
public. We did not include this
requirement in the 2005 proposed rule.
Under the prior version of
§ 816.116(a)(1), States were required to
include selected standards and
techniques in their approved programs
but were not required to include them
in the rules of their approved programs.
Rather, States had the option of
including them in any element of their
approved programs including
guidelines, technical procedures, policy
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51691
materials, etc. States will continue to
have the option of including selected
success standards and sampling
techniques in the same range of formats,
but must ensure their public
availability. For example, States could
make this information available to the
public at places where other documents
such as permit applications are also
made available for public review. Or the
States could further make it available to
all interested parties either by mail or
through the agency’s web site. As
before, States will continue to have the
option of including selected standards
and techniques in their approved
program regulations. Whatever the
formats chosen by the States, final
§ 816.116(a)(1) ensures the public access
to and, therefore, the ability to review
the selected standards and techniques.
Furthermore, there will continue to be
ample opportunity on a permit-specific
basis for public review of the proposed
use of selected standards and sampling
techniques both during the permitting
process as well as at bond release.
Because § 780.18(b)(5) requires each
permit application to identify its
proposed success standards and
sampling techniques, this information is
also available for public review. Parties
who have an interest that may be
adversely affected by a decision on the
application may further comment on
these standards and sampling
techniques under § 773.6(a) and (b)(2).
These provisions ensure that the public
will continue to have the ability to
review the success standards and
sampling techniques for every mine
before operations begin. In addition, any
persons with valid legal interests can
also object to bond release under
§ 800.40(f) should they believe the
operator has not used the approved
success standard or not followed the
approved sampling techniques.
Three of the five commenters
opposing removal of the approved
program requirement from
§ 816.116(a)(1) warned against the
disputes that they asserted would
inevitably arise between States and
permit applicants/operators and
between operators and landowners over
what constitutes appropriate success
standards and/or sampling techniques.
The first of these three commenters
admitted that the proposed revision
would provide flexibility to State
programs and would allow both States
and operators to take advantage of new
technology, sample methods, and
statistics. This commenter also
conceded that the approved program
requirement of § 816.116(a)(1) was
unnecessarily burdensome in terms of
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the time and resources required by the
State program amendment process and
that this burden discourages updating
revegetation standards. Nonetheless,
this commenter asserted that any
flexibility gained by the proposed
revision to 816.116(a)(1) would not
offset the endless disputes that would
inevitably arise between States and
permit applicants over what constitute
acceptable methods and statistics.
While we believe that this commenter
overstates the potential for disputes
between States and permit applicants
under proposed § 816.116(a)(1), final
§ 816.116(a)(1) expressly requires that
all State-selected standards and
techniques be in writing and made
available to the public. This new
provision should minimize disputes
between a State and applicants over the
range of success standards and sampling
techniques available within that State.
As under the prior rule, the permit
applicant will be able to choose only
from among available success standards
and sampling techniques previously
selected by the State. As under the prior
rule, moreover, an applicant’s proposed
use of a selected standard or technique
will be subject to State approval.
Importantly, the potential for disputes
between the regulatory authority and
permit applicant should not be any
greater than under the prior rule.
Two of the five commenters expressed
additional concerns over the potential
conflict that might arise between
landowners and operators as a result of
the proposed revision to § 816.116(a)(1).
One of these two commenters also
declared that the deletion of the
approved program requirement would
potentially place the landowner and
operator in conflict at the time of bond
release due to the use of measurement
standards that lack a robust scientific
basis.
We do not believe that the deletion of
the approved program requirement from
§ 816.116(a)(1) will materially raise the
potential for conflict between the
landowner and operator at the time of
bond release. As stated earlier, the
provisions of § 816.116(a)(2) and (b) will
continue to establish clear criteria and
requirements for the success standards
and sampling techniques that may be
selected by the States under
§ 816.116(a)(1). All approved programs
have counterparts to § 816.116(a)(2) and
(b). Accordingly, the success standards
and statistically valid sampling
techniques selected by a State under
final § 816.116(a)(1) will, for the
purposes of establishing revegetation
success at bond release, have the same
robust scientific basis as the standards
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and techniques selected by the State
under the prior rule.
One of the commenters opposing
removal of the approved program
requirement from § 816.116(a)(1)
suggested that, without including
success standards and measuring
techniques in the approved State
program, operators may simply choose
not to comply with selected standards
and techniques.
With regard to this concern, we note
that all State approved programs have
counterparts to § 780.18(b)(5) requiring
that applications for a permit contain a
plan for revegetation, including
measures to determine the success of
revegetation. Once approved by the
regulatory authority, these and all other
permit terms are binding and
enforceable.
Still another commenter asserted that
the reasons given by us for this removal
do not support abrupt departure from
more than two decades of regulatory
policy.
We disagree. The reasons provided in
both this and the proposed rulemaking
more than adequately support the
revision. It is our agency’s continuing
policy to examine existing regulations
and to make changes that reduce the
burden on State regulatory authorities,
OSM, the industry, or the public while
assuring the achievement of SMCRA’s
purposes and requirements. The current
regulatory change is intended to reduce
the burden on regulatory authorities and
OSM without hindering the
achievement of the SMCRA requirement
that coal mining and reclamation
operations establish a diverse,
permanent, and effective vegetative
cover on all affected lands. 30 U.S.C.
1265(b)(19) and 1266(b)(6). This
provision says nothing about success
standards, sampling techniques, or
whether those details must be in a State
program.
In our 1983 rulemaking we allowed
use of only those revegetation success
standards and measurement techniques
that have been incorporated into the
approved program. See 48 FR 40160,
September 2. An agency’s rules once
adopted are, however, not frozen in
place. An agency may alter its rules in
light of its accumulated experience in
administering them when it determines
that a different approach would better
implement the statutory scheme. As
discussed above, our experience over
the last twenty years indicates that the
approved program requirement poses an
unnecessary obstacle to technological
innovation and adoption of new
standards and sampling techniques.
State programs have matured and can be
relied upon to meet the requirements of
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SMCRA in light of the nationwide
minimum requirements at
§ 816.116(a)(2) and (b) that will remain
in place and will serve as a regulatory
floor. Moreover, the Fourth Circuit has
admonished us that, ‘‘in contrast to
other ‘cooperative federalism’ statutes,
SMCRA exhibits extraordinary
deference to the States.’’ See Bragg v.
West Va. Coal Ass’n, 248 F.3d 275, 293
(4th Cir. 2001). Thus, even if it might be
permissible for us to continue to require
that revegetation success standards and
sampling techniques be approved as
part of the State regulatory program, it
is nonetheless reasonable and
appropriate for us to allow the States to
make changes to those details without
our involvement, as long as each State
meets and implements the minimum
nationwide standards.
Three of the five commenters
opposing the proposed rule took issue
with the statement in our 2005 preamble
that the ‘‘relatively cumbersome’’ nature
of the State program amendment
process may discourage States from
utilizing ongoing research findings and
technological advances to adopt new
and improved success standards and
sampling techniques. The first of these
commenters admitted that its own
regulatory review process is
cumbersome, but stated that that is
because, in many cases, OSM is trying
to ‘‘dodge a political bullet,’’ rather than
working in a more expeditious manner.
The second commenter indicated that
the fact that the State program
amendment process is cumbersome is
the result of OSM’s decision not to more
timely process State program changes.
The same commenter noted that there is
nothing inherently cumbersome or slow
about the State program amendment
process. The commenter also stated that
OSM should be able to timely review
and approve a properly documented
State program amendment without
hampering State innovation. In closing,
this commenter asserted that the
‘‘cumbersome’’ nature of the current
State program amendment process is a
result of Federal agency practice, since
the commenter saw nothing inherent in
that process that requires the sort of
delay that has attended OSM’s review of
program amendments. The third
commenter stated that maintaining the
current State program provisions would
not stifle evaluation or utilization of
new techniques. This commenter
suggested that, as an alternative to
eliminating the requirement that success
standards and sampling techniques be
included in the approved program, OSM
should rather streamline its own
program amendment review process so
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as to assure that when proposed
program amendments are supported by
technological advances, they are
processed and approved in an expedited
fashion.
We strongly disagree with the general
conclusion of these comments that any
delay in the State program amendment
process is attributable to our failure to
timely process State program
amendments. We recognize that we can
make incremental improvements to
speed the processing of State program
amendments at the Federal level.
However, the requirement that we
approve amendments to these programs
requires steps that are inherently time
consuming. Also, a State may be
required to go through its own
rulemaking process before proposing
amendments to its approved program
under § 732.17. This State rulemaking
process can also be very time
consuming and is a practice over which
we have no control. Accordingly, the
deletion of the approved program
requirement from § 816.116(a)(1) should
enable States to more quickly adopt
improved success standards and
sampling techniques.
Three of the five commenters
opposing the proposed rule asserted that
the proposed deletion of the approved
program requirement from
§ 816.116(a)(1) would undermine the
core requirement in the Act that the
Secretary establish a comprehensive set
of minimum Federal standards for
approved programs. Commenters also
alleged that continued OSM prior
review and approval of selected
standards and sampling techniques was
needed to assure a level playing field
among States.
We do not believe these concerns are
well-founded. The change to final
§ 816.116(a)(1) does not delete any
statutorily-prescribed minimum
standards. Section 101(f) of SMCRA
provides that ‘‘because of the diversity
in terrain, climate, biologic, chemical,
and other physical conditions in areas
subject to mining operations, the
primary governmental responsibility for
developing, authorizing, issuing, and
enforcing regulations for surface mining
and reclamation operations subject to
this Act should rest with the States.’’ 30
U.S.C. 1201(f). In turn, section
515(b)(19) of SMCRA expressly provides
that a State’s performance standards
shall require surface coal mining and
reclamation operations as a minimum to
‘‘establish on the reg[ra]ded areas, and
all other lands affected, a diverse,
effective, and permanent vegetative
cover of the same seasonal variety
native to the area of land to be affected
and capable of self-regeneration and
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plant succession at least equal in extent
of cover to the natural vegetation of the
area * * *.’’ 30 U.S.C. 1265(b)(19).
In implementing these two statutory
provisions, both our prior rule as well
as our proposed and final rules at
§ 816.116(a)(1) require States to select
revegetation success standards and
sampling techniques subject to the
general conditions of § 816.116(a)(2) and
(b). In turn, § 816.116(a)(2) specifically
requires that State-selected sampling
techniques for measuring success use a
90-percent statistical confidence
interval and § 816.116(a)(2) and (b)
require that State-selected success
standards accord with the vegetative
cover or crop production of appropriate
reference areas.
We see nothing in these statutory and
regulatory authorities to support
commenters’ assertion that OSM’s prior
review of selected standards and
techniques was needed to assure a level
playing field among States. State
compliance with the criteria of
§ 816.116(a)(2) and (b) will, however,
continue to ensure that a relatively level
playing field exists among States. None
of the revisions in final § 816.116(a)(1)
will jeopardize State compliance with
the criteria of § 816.116(a)(2) and (b).
Two commenters expressed concern
about the negative effect that the
proposed rule would have on the
adequacy of reclamation required for
bond release. The first of these
commenters warned that, if States are
no longer obligated to identify and
defend their choice of objective
standards for determining revegetation
success, those States might adopt
standards that are not based on good
science in order to facilitate bond
release. The second of these
commenters declared that the proposed
rule would allow operators to apply
whatever standards they desired and
that lands that did not meet the
longstanding reclamation requirements
of the Act would be released from their
reclamation bond.
In partial response to these concerns,
the final rule requires that success
standards and sampling techniques
selected by the States be in writing and
made available to the public. As
previously noted, this requirement
should substantially relieve
commenters’ concerns that operators
could apply whatever standard they
desire and should also allay much of
commenters’ fears as to inconsistent
standards among individual States. As
set forth in our 2005 proposed rule (70
FR 13076, 13081), we continue to
believe that the criteria enunciated in
§ 816.116(a)(2) and (b) will preclude
States from selecting inadequate success
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standards or sampling techniques for
which there is no sound scientific basis.
For the same reasons, we continue to
believe that appropriate reclamation
will, as before, be required for bond
release. The bond release and oversight
protection provided at §§ 800.40(b)(1)
and 733.12(a)(1) should also, as under
the prior rule, further guard against
faulty bond release. With the same
general protections in place as before,
final § 816.116(a)(1) will merely allow a
State program to employ the latest and
most appropriate standards and
sampling techniques without first
having to go through the timeconsuming process of adding them to its
approved regulatory program.
One commenter also asserted that, if
every permit had its own revegetation
standards and measurement techniques,
it would be extremely difficult for even
the most dedicated State regulator to
keep track of the approved success
standards and sampling techniques and
to use them for evaluating revegetation
success.
The new requirement of final
§ 816.116(a)(1) that the success
standards and sampling techniques
selected by the regulatory authority be
in writing and be made available to the
public should ensure that the number of
new standards and sampling techniques
that the State regulator must keep track
of and use remain at a reasonably
manageable number.
Two commenters alleged that our
oversight of State programs would not
be adequate to catch problems with
success standards and sampling
techniques. The first of these
commenters challenged our statement in
the 2005 preamble that the oversight
process would directly address any
major deficiency identified in the
revegetation success standards and/or
sampling techniques used by a State.
The second of these commenters
questioned whether OSM would be
familiar enough with all the differences
between possible success standards and
sampling techniques to be able to
determine which one was deficient.
We disagree with these concerns as to
our oversight authority and capacity to
identify and address major deficiencies
in the success standards and/or
sampling techniques selected by the
States. The revision to final
§ 816.116(a)(1) does not restrict or in
any way impair our continuing
authority under § 733.12(a)(1) to
annually evaluate the administration of
individual approved programs. These
evaluations address programmatic
problems and are conducted in
accordance with longstanding agency
policies that focus on the on-the-ground
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results of reclamation and revegetation
activities. From our past experience, we
are confident that there are sufficient
numbers of knowledgeable OSM
personnel, including inspectors,
committed to evaluating each State’s
reclamation performance. If our field
reviews identify problems with
inappropriate State evaluations of
revegetation success, we will then
review the permits in question to
determine whether the correct success
standards and sampling techniques
were used in those evaluations. This
review could, if appropriate, also
address whether the success standards
and sampling techniques complied with
the State counterparts to § 816.116(a)(2)
and (b). If we find that they are not in
compliance, then we will work with the
State to correct deficiencies, ensuring
that all success standards and sampling
techniques comply with program
requirements.
Three of the five commenters
opposing the proposed rule also
disagreed with our assertion that the
approved program requirement of
§ 816.116(a)(1) in the previous
regulation discourages the use of new
technologies. One of these commenters
stated that our call for use of the latest
sampling techniques was inappropriate.
This commenter indicated that we
should instead seek the most accurate
and reliable sampling techniques rather
than the ‘‘latest thing’’ in new sampling
techniques, which might not be the best
for the particular circumstance. The
commenter further indicated that we
should provide a backstop against fads
that can sweep a scientific community.
The commenter questioned our agency’s
concern to have the ‘‘latest thing’’ in
sampling techniques available when we
showed so little interest in the latest
scientific ‘‘thing’’ in blasting. The
commenter observed that, according to
our explanation for eliminating the
approved program requirement of
paragraph (a)(1), OSM and some of the
States were experimenting with new,
potentially useful methods, but that it
would take time to determine their
reliability. The commenter warned that,
until we made that determination, we
should not dump proven practices in
favor of the latest technology.
We disagree with these concerns. The
Federal regulations at § 816.116(a)(2)
and their State counterparts clearly
require that all statistically valid
sampling techniques must use a 90percent confidence interval. This
requirement will ensure that, regardless
of the individual technique selected by
the regulatory authority, all selected
techniques will require the same level of
precision. Our experience has shown
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that State personnel have both the
expertise and experience to determine
the reliability of new sampling
techniques. Eliminating the approved
program requirement from
§ 816.116(a)(1) will, therefore, enable
regulatory authorities to more quickly
adopt new and reliable techniques, but
will not require States to make changes
should they be satisfied with their
existing techniques.
Another of the commenters stated that
OSM’s goal of allowing variance among
legitimate methods of measuring
revegetation success could still be met
through the State program amendment
process but cautioned that the standards
for measuring success do not change so
dramatically and rapidly as to
necessitate ‘‘streamlining’’ State
adoption of new measurement
techniques by eliminating OSM and
public review.
As we stated previously, the time
involved in the program amendment
process is substantial and does not
allow expedited implementation of new
measurement technologies in approved
State programs. We have also explained
that the final rule will not eliminate
public access to information about new
measurement techniques selected by the
States, nor will it impair our oversight
of State evaluations of revegetation
success. While public involvement in
such changes will be different than
under the prior rule, as will be our
involvement, we believe the changes
will fully, and more efficiently
implement the requirements of SMCRA.
After considering the benefits and costs
of removing the approved program
requirement from § 816.116(a)(1), we
have concluded that both the
environment and good science would be
appropriately served by its removal.
One commenter was concerned that,
without the Federal requirement for
including selected success standards
and measuring techniques in States’
approved programs, States that have a
‘‘no more stringent than’’ clause in their
State law may feel constrained not to
adopt such standards and techniques as
a matter of State regulation.
We disagree with the commenter’s
concern that the existence of a ‘‘no more
stringent than’’ clause in a State law
will result in the State not adopting
success standards and measuring
techniques. Revised § 816.116(a)(1) does
not change its requirement that a State
must still select success standards and
sampling techniques for use in its
program. Furthermore, these selected
standards and techniques must continue
to be consistent with the Secretary’s
regulations, particularly with the
requirements of § 816.116(a)(2) and (b).
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A ‘‘no more stringent’’ clause in the
State’s approved program would not
negate any of these requirements.
Two commenters stated that
§ 816.116(a)(1) does not need to be
changed in order for a State’s success
standards to address the variability of
environmental conditions found in that
State. While we acknowledge the truth
of this statement, the principal
motivation for our changing
§ 816.116(a)(1) continues to be reducing
the time that may be required before a
State program may adopt the latest,
scientifically responsible standards for
revegetation success.
One commenter asserted that removal
of the approved program requirement
from § 816.116(a)(1) also removes the
‘‘force of rule’’ from the sampling
techniques selected by the regulatory
authority.
In response, we note that final
§ 816.116(a)(1) does not change the
requirement for States to select the
standards for success and statistically
valid sampling techniques. Under the
prior rule, however, the standards and
techniques selected by a State were
required to be included in the approved
program but were not required to be in
rule form. As discussed above, these
standards and techniques could also
have been included in a guideline or
other statement of technical procedures.
Under final § 816.116(a)(1), States will
still have those options; but selected
standards and techniques will have to
be made available to the public.
Another commenter took issue with
the statement in our 2005 proposed rule
that the existing requirements of
§ 816.116(a)(2) and (b) should ensure
that selected success standards and
sampling techniques used in the various
States will provide similar degrees of
proof that adequate reclamation has
been achieved. The commenter
disagreed with this assessment,
indicating that, while standards for
success are specified in these sections,
the only specification regarding
sampling methods is that parameters
must be evaluated using sampling
techniques with a 90-percent statistical
confidence interval. The commenter
added that the application of a
statistical confidence limit is merely the
final step in a long process, with no
requirements being established in the
rule for the intermediate steps in this
process. While the commenter observed
that there are many ways to obtain a
data set for evaluation that meets the
requirement for sampling using a 90percent confidence interval, he noted
that many of these ways do not, for
various reasons, constitute a
representative sample of the target
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population. In addition, there are many
different types of statistical tests that
might be applied to determine 90percent confidence. The commenter
further stated that inappropriate
application of statistical tests would
result in incorrect conclusions regarding
eligibility of lands for bond release. The
use of sampling methods and statistical
tests with no rules on approved
methods would inevitably result in
incorrect decisions regarding bond
release and inconsistent application of
rules and standards. In conclusion, this
commenter declared that the premise
that a regulatory authority will be able
to ensure appropriate use of sampling
methods and statistics without those
requirements being included in the
approved program is entirely
unrealistic.
The commenter is correct in its
statement that there are many ways to
obtain data satisfying the required 90percent statistical confidence interval
that may not constitute a representative
sample of the target population.
Similarly, there are many types of
statistical tests that might be applied to
determine the 90-percent statistical
confidence interval. Inappropriate
application of these statistical tests
could, as the commenter suggested,
result in incorrect conclusions regarding
the eligibility of lands for bond release.
The framing and the appropriate
application of these sampling methods
and statistical tests have always been
two of the challenges facing the State
regulatory authority under the prior
rule. The same challenges will continue
under the new rule. The only ‘‘rule,’’
i.e., regulatory prescription, that has
ever governed the selection and
application of sampling techniques and
statistical tests is the 90-percent
statistical confidence interval of
§ 816.116(a)(2). This requirement will
not be affected by the revision to
§ 816.116(a)(1). Accordingly, we
strongly question the commenter’s
broad declaration that without ‘‘rules’’
on approved methods, incorrect
decisions regarding bond release and
inconsistent application of rules would
‘‘inevitably result.’’ As stated above, it
furthermore has been our experience
that States have the necessary technical
expertise both to select statistically
valid sampling techniques and
statistical tests that would result in a
representative sample of the target
population and to ensure that the
statistical tests are applied correctly. As
before, we will be available to provide
technical assistance to the States in any
further development and application of
statistically valid sampling techniques
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and statistical tests. While not absolute
guarantees in themselves, we reasonably
believe that the current rules at
§ 816.116(a)(2) and the current level of
State expertise will continue to provide
for appropriate development and use of
sampling methods and statistics.
Apparently in response to the
statement in our 2005 preamble that our
regulations allow technical standards to
be included in technical guidance
documents that are not part of the
approved regulatory program, one
commenter questioned whether any
outside party had access to our
‘‘records’’ as the regulatory authority in
Tennessee, Washington, and for the
Indian Lands Programs. All permitting
actions and bond releases in Tennessee,
Washington and on Indian Lands are, in
fact, available for public review. All
reclamation plans, including
revegetation success standards and
sampling techniques, for permits in
Tennessee and Washington and on
Indian Lands are also available for
public review. Arrangements may be
made to review those records by
contacting the appropriate OSM office.
3. Section 816.116(b)(3): Success
Standards for Undeveloped Land
What are the revisions to
§ 816.116(b)(3)?
We have revised § 816.116(b)(3) to
add undeveloped land as one of the
land uses subject to that section’s
success standards. Revised
§ 816.116(b)(3) will read as follows,
with new language in italics:
For areas to be developed for fish and
wildlife habitat, recreation, undeveloped
land, or forest products, success of vegetation
shall be determined on the basis of tree and
shrub stocking and vegetative ground cover.
This provision is identical to that
proposed in our 2005 Federal Register
notice.
The basis for our revision to
§ 816.116(b)(3) is set forth in detail in
that notice. There we noted that several
commenters responding to our 1999
outreach had suggested that current
§ 701.5 includes undeveloped land as a
land use category and defines it as ‘‘land
that is undeveloped or, if previously
developed, land that has been allowed
to return naturally to an undeveloped
state or has been allowed to return to
forest through natural succession.’’
Therefore, without any change to the
current regulations, undeveloped land
can be approved as a postmining land
use under the postmining land use
provisions of § 816.133. However,
unlike all the other land use categories
listed in § 701.5, undeveloped land does
not have success standards specified in
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§ 816.116(b). Under this final rule, the
inclusion of undeveloped land among
the land uses subject to the revegetation
success standards of § 816.116(b)(3) will
mean that undeveloped land will be
subject to cover and, if applicable,
stocking requirements depending on the
vegetation goals for each parcel of land.
We consider the cover and stocking
requirements of § 816.116(b)(3) to be
particularly appropriate criteria for
evaluating the revegetation success of an
undeveloped land use area, as they can
be used to ensure the establishment of
the seral species, i.e., a community of
mixed grasses, forbs, shrubs and trees,
necessary to facilitate natural plant
succession.
What were the comments submitted on
our proposed revision to
§ 816.116(b)(3)?
Eight commenters supported the
proposed revision of § 816.116(b)(3) to
add undeveloped land as one of the
land uses subject to that section’s
success standards. These commenters
were in general agreement that having
undeveloped land available as a
postmining land use could allow
reclamation of areas that potentially
provide higher ecological benefits and
diversity (and reforestation) than the
other land uses previously identified in
the regulations at § 816.116(b).
One of these commenters asked
whether the seral species on
undeveloped land must be
predominately native to the area or
whether large swaths of introduced
species, such as kudzu, could be
acceptable in States such as Tennessee
or Alabama.
As previously noted, undeveloped
land is defined as ‘‘land that is
undeveloped or, if previously
developed, land that has been allowed
to return naturally to an undeveloped
state or has been allowed to return to
forest through natural succession.’’
Therefore, if an operator chooses
undeveloped land as a postmining land
use, we believe that the operator would
have to reclaim the land with the
revegetation goal of promoting natural
succession. In this regard, the
revegetation provisions of § 816.111
require the use of species native to the
area, or of introduced species where
desirable and necessary to achieve the
approved postmining land use. The use
of those introduced species must also be
approved by the regulatory authority,
and under § 816.111 those species must
be capable of plant succession. Species
like kudzu that are considered noxious
weeds could not be introduced because
of the prohibitions of State and Federal
laws and regulations governing noxious
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plant and introduced species. It would
not be feasible or appropriate for us to
establish national standards for seral
species because of the vast differences
in plant communities throughout the
country. Planting and seeding plans for
development of seral plant communities
is best done at the local level by
professionals most familiar with the
local environment.
Another commenter noted that the
Ohio approved program has established
a postmining success standard for
undeveloped lands. The intended
purpose of that program regulation was
to encourage the planting of trees and
shrubs without the need to achieve an
established standard for stems per acre,
survival or plant productivity. The
commenter observed that, in spite of
this incentive, the Ohio regulation has
not proven successful in encouraging
additional tree and shrub plantings
within mined areas. Based on this Ohio
experience, the commenter stated that
the proposed revision to include
undeveloped land among the listed land
uses of § 816.116(b)(3) is unnecessary as
the inclusion is not likely to achieve its
intended purpose of encouraging tree
and shrub planting. Instead, the
commenter recommended the
establishment of a national standard
requiring that a minimum of 80 percent
of the acreage that is disturbed by
mining and that supported a forest or
shrub cover prior to mining must be
reclaimed to forest and shrub cover
following mining. The commenter based
this recommendation on several States’
interpretation of their existing rules.
The commenter further stated that this
restoration requirement for forest and
shrub lands would necessitate the
development and utilization of
techniques necessary to ensure
successful restoration of premine land
use capabilities, including those of
forestry or fish and wildlife habitat.
Such a national requirement would also
establish a consistent playing field for
operators across the country.
We appreciate the commenter’s
concern as to whether the Ohio rules
have been successful in encouraging
tree and shrub planting on undeveloped
land. Nonetheless, because undeveloped
land is already available as a postmining
land use, we believe that it is necessary
both to establish revegetation success
parameters for this land use and to
require that operators, to obtain bond
release, then demonstrate compliance
with those parameters. Revising
§ 816.116(b)(3) to include undeveloped
land among the numbered postmining
land uses assures that all approved
postmining land uses will have to meet
prescribed revegetation success
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standards. The commenter’s proposal to
require reclamation to premining cover
type of 80 percent of the acreage that
previously supported a forest or shrub
cover goes beyond the requirements of
SMCRA. Section 515(b)(2) of the Act
addresses postmining land use and
requires restoration of affected lands to
a condition capable of supporting the
uses which it was capable of supporting
prior to any mining, or higher or better
uses. The proposed establishment of
national criteria requiring redistribution
of a particular level of premine tree and
shrub cover is therefore not authorized,
because SMCRA allows landowners to
choose higher or better postmining land
uses.
Two commenters contended that
OSM should do more than simply
adding undeveloped land to the list of
land uses subject to the requirements of
§ 816.116(b). They argued that, if OSM
finalizes its proposal, the new rule
would not foster one of our stated
objectives which was to encourage
reforestation. These commenters
asserted that some permit applicants
would choose not to select undeveloped
land as their postmining land use and
would propose not to plant trees if the
revegetation standards for undeveloped
land were unnecessarily burdensome.
Moreover, these commenters noted that,
in approving Ohio’s success standards
for undeveloped land, we stated that
‘‘undeveloped land is consistent with
the Federal regulations which do not
contain specific success standards for
undeveloped land, and is in keeping
with section 101(f) of SMCRA, which
vests the States with the primary
governmental responsibility for
developing, authorizing, issuing, and
enforcing regulations for surface coal
mining and reclamations operations.’’
59 FR 22514, May 2, 1994.
The same two commenters indicated
that, instead of treating the undeveloped
land category like the other land uses in
§ 816.116(b)(3), OSM should recognize
that the State regulatory authority may
develop its own undeveloped land
revegetation success standards on a
program-wide or individual permit
basis. Such State-specific revegetation
success standards for undeveloped land
would, of course, ensure that the land
be allowed to return to its natural or
undeveloped state, or to forest through
natural succession. The commenters
suggested using the Ohio approved
program as a model for development of
future Federal regulations. Under this
approach, revegetation success for the
undeveloped land use would be
determined on the basis of ground cover
and the proper planting of appropriate
tree and shrub species specified in the
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permittee’s approved planting plan. In
addition, these commenters suggested
that revegetation on undeveloped land
should be found successful for phase II
bond release when the herbaceous
ground cover species are established
and provide sufficient ground cover to
control erosion. For phase III, the bond
should be released when the five-year
period of responsibility has expired and
acceptable species of trees and shrubs
have been properly planted in
accordance with the approved planting
plan. The commenters indicated that
survival of tree or shrub plantings
should not be a requirement for phase
III bond release, as long as the permittee
demonstrates that the planting plan has
been approved and followed and that
trees and shrubs have been planted in
approved numbers and locations. The
commenters affirmed that this proposed
regulatory approach to revegetation
success for undeveloped land would
encourage more reforestation than
OSM’s proposal to include undeveloped
land among the land uses subject to the
revegetation success standards of
§ 816.116(b)(3).
We do not agree with any aspect of
the commenters’ proposal. As noted in
the preamble to the proposed rule,
unlike all the other land use categories
listed in § 701.5, undeveloped land does
not have specified revegetation success
standards in § 816.116(b). The inclusion
of undeveloped land as one of the land
uses subject to the success standards of
§ 816.116(b)(3) means that undeveloped
land will, like all the other listed land
uses, have specific revegetation success
standards. Therefore, any area with an
approved undeveloped land use will be
subject to the cover and, if applicable,
stocking requirements of § 816.116(b)(3)
depending on the particular vegetation
goals set for that parcel of land. These
cover and stocking requirements are
particularly appropriate criteria for
evaluating the revegetation success of an
undeveloped land use area as these
requirements should ensure the
establishment of the seral species, i.e., a
community of mixed grasses, forbs,
shrubs and trees, necessary to facilitate
natural plant succession. Upon
promulgation of this final rule, if
reforestation proves to be the desired
goal of individual revegetation efforts,
the approved land uses could be forest
products (forestry), fish and wildlife
habitat, or undeveloped land. For phase
II bond release the operator must only
demonstrate the establishment of the
seeded or planted species. However, we
maintain that in all cases, and for
obvious reasons, the ultimate success of
revegetation when it is evaluated at
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phase III must be based on cover and the
survival of the planted trees, not simply
the planting of those trees. Under both
the prior and final rule the specific
success standards and criteria used to
evaluate each of these land uses will be
established by the regulatory authority.
We note that, contrary to these latter
commenters’ assertions about the
efficacy of the Ohio model in
encouraging reforestation, Ohio has
indicated that its approved provisions
for evaluating revegetation success for
undeveloped land, which do not require
evaluation of survival, have not been
successful in encouraging tree and
shrub planting. We do not believe that
including survival requirements for
trees in the success standards for
undeveloped land will adversely affect
reforestation efforts. In sum, we find no
meaningful basis for exempting the
undeveloped land use from the success
requirements common to all other land
uses listed in § 816.116(b).
4. Section 816.116(b)(3): Shelter Belts
What are the revisions to
§ 816.116(b)(3)?
We are further revising the
revegetation success provisions of
§ 816.116(b)(3) to eliminate the
reference to shelter belts from listed
land uses. This revision is identical to
that in the 2005 proposed rule. We will
address the use of shelter belts under
the revegetation success provisions of
§ 816.116(c)(4), which governs normal
husbandry practices.
As discussed in the preamble to that
proposed rule, we have removed shelter
belts from the land uses listed in
§ 816.116(b)(3) for three reasons: shelter
belts have never been included among
the land use categories listed in § 701.5;
shelter belts are defined as conservation
practices, not land uses, by the Natural
Resources Conservation Service (NRCS);
and the recognized purpose and ongoing
maintenance requirements of shelter
belts are consistent with the normal
husbandry practices allowed by
§ 816.116(c)(4).
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What were the comments submitted on
our proposed revision to
§ 816.116(b)(3)?
Ten commenters supported removing
shelter belts from the land uses listed in
§ 816.116(b)(3). All these commenters
agreed with our position that shelter
belts are conservation practices and
should, therefore, be addressed as
normal husbandry practices.
One commenter opposed the
proposed revision, preferring that the
reference to shelter belts be retained in
our regulations at § 816.116(b)(3). This
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commenter stated that the underlying
idea behind the (b)(3) regulation has
been that shelter belts would provide
cover for game traveling between
different kinds of postmining land uses
and would aid in controlling wind and
water erosion. The commenter indicated
that we should retain the idea of
providing cover for game and
controlling erosion with tree and shrub
plantings, even within areas reclaimed
for residential, commercial, or industrial
postmining land uses. The commenter
contended that, if the idea of providing
cover for game and controlling erosion
with tree and shrub plantings is lost by
removing shelter belts from among the
listed land uses of § 816.116(b)(3), we
would be bowing to the ‘‘barrenness’’ of
those uses. While the commenter agreed
that the NRCS definition of shelter belt’’
may be a husbandry practice, he noted
that the shelter belt concept, as
currently used in our regulations,
involves more than a mere husbandry
practice and should be retained in
§ 816.116(b)(3).
We agree that, to provide habitat for
various wildlife species as well as to
control wind and water erosion, we
should encourage the use of shelter
belts. However, the inclusion of shelter
belts among listed land uses in
§ 816.116(b)(3) triggers a statistical
evaluation of shelter belts under
§ 816.116(a)(2) for determining
revegetation success at bond release. We
believe that requiring such a statistical
evaluation actually discourages the use
of shelter belts on reclaimed lands
because of the time and money
necessary for sampling and preparing a
bond release application. Not
surprisingly, the current use of shelter
belts is very limited. Redesignation of
shelter belts as a normal husbandry
practice should reasonably encourage
their future use and proper
maintenance.
In response to the commenter’s
concern about the value of shelter belts
as wildlife cover, we note that the
Federal regulations at § 816.97(a)
continue to require that the operator
must, to the extent possible and using
the best technology currently available,
minimize disturbances and adverse
impacts on fish, wildlife, and related
environmental values and must enhance
such resources where practicable.
Furthermore, § 816.97(h) continues to
require that, where cropland is to be the
postmining land use and where it is
appropriate for wildlife- and cropmanagement practices, the operator
must intersperse fields with trees,
hedges, or fence rows throughout the
harvested area to break up large blocks
of monoculture and to diversify habitat
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51697
types for birds and other animals.
Finally, § 816.97(i) requires that, where
residential, public service, or industrial
uses are to be the postmining land use,
and, where it is consistent with the
approved postmining land use, the
operator shall intersperse reclaimed
lands with greenbelts utilizing species
of grass, shrubs, and trees useful as food
and cover for wildlife. In answer to the
commenter’s general concerns, these
cited regulations clearly provide for the
use of vegetated areas similar to shelter
belts for enhancing wildlife habitat,
even with residential or industrial
postmining land uses.
Another commenter supported the
proposed changes, agreeing that shelter
belts are not a land use but rather a
conservation practice supporting
approved land uses. Nonetheless, this
commenter argued that any trees
included in the shelter belt area should
still be subject to the requirement at
§ 816.116(b)(3)(ii) that, at the time of
bond release, at least 80 percent of the
trees and shrubs used to determine such
success shall have been in place for 60
percent of the applicable minimum
period of responsibility and all shall
have been in place for at least two years
(the ‘‘80/60 rule’’). Accordingly, the
commenter suggested that language be
included in the regulations to clarify
that shelter belts are subject to the
success standard of § 816.116(b)(3)(ii).
In response to this comment, we note
that it would be logically inconsistent to
treat shelter belts as normal husbandry
practices, which allow for maintenance
that could include dead tree or shrub
replacement, irrigation, thinning,
pruning, chemical application for
disease and pests, protection from
livestock and wildlife, and fertilization,
but still require shelter belts to comply
with the 80/60 rule, which places limits
on tree and shrub replanting.
5. Section 816.116(b)(3)(ii): Tree and
Shrub Stocking Standards
What are the revisions to
§ 816.116(b)(3)(ii)?
We have made three minor revisions
to § 816.116(b)(3)(ii) to provide new
ways in which operators may accurately
satisfy the existing revegetation success
standards of the 80/60 rule for areas
developed for fish and wildlife habitat,
recreation, undeveloped land, or forest
product postmining land uses. Revised
§ 816.116(b)(3)(ii) will read as follows,
with new language in italics:
(ii) Trees and shrubs that will be used in
determining the success of stocking and the
adequacy of the plant arrangement shall have
utility for the approved postmining land use.
Trees and shrubs counted in determining
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such success shall be healthy and have been
in place for not less than two growing
seasons. At the time of bond release, at least
80 percent of the trees and shrubs used to
determine such success shall have been in
place for 60 percent of the applicable
minimum period of responsibility. The
requirements of this section apply to trees
and shrubs that have been seeded or
transplanted and can be met when records of
woody vegetation planted show that no
woody plants were planted during the last
two growing seasons of the responsibility
period and, if any replanting of woody plants
took place during the responsibility period,
the total number planted during the last 60
percent of that period is less than 20 percent
of the total number of woody plants required.
Any replanting must be by means of
transplants to allow for adequate accounting
of plant stocking. This final accounting may
include volunteer trees and shrubs of
approved species. Volunteer trees and shrubs
of approved species shall be deemed
equivalent to planted specimens two years of
age or older and can be counted towards
success. Suckers on shrubby vegetation can
be counted as volunteer plants when it is
evident the shrub community is vigorous and
expanding.
The revised language is identical to
that included in our 2005 proposed rule.
As discussed in the preamble to that
rule, many mine operators over the
years have perceived the 80/60 rule as
not only being complex and confusing
but also subject to uncertain
implementation by State regulatory
authorities. Furthermore, operators
often perceived as unnecessarily
difficult, costly, and time-consuming
the need under the 80/60 rule for
determining the length of time that
individual trees and shrubs have been
in place. In response to these concerns,
we have added five sentences to the end
of the existing language of
§ 816.116(b)(3)(ii) to implement three
minor revisions in the way operators
may satisfy the 80/60 success standards.
The first revision to
§ 816.116(b)(3)(ii), represented by the
first two new sentences added to the
end of existing rule language, effectively
eliminates the current potential need
under the 80/60 rule for field
verification of the time in place of
individual plants. Under the prior rule,
especially in areas of greater than 26
inches of average annual precipitation
(‘‘humid areas’’) where mined land
could reasonably be reforested, the need
for determining the time in place of
trees has proven to be a significant
disincentive to reforestation. Instead,
operators have tended to choose grazing
land or pastureland, not forestry, in
order to avoid application of the treecounting requirements of the 80/60 rule.
With our first revision to
§ 816.116(b)(3)(ii), operators can now
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document compliance with the 80/60
rule time-in-place requirements for
individual plants by comparing records
of initial planting (or ‘‘stocking’’) and
replanting of transplants to the final
field count of plants at bond release.
The second sentence specifically
requires the use of transplants rather
than seeding for any replanting. We
have added this requirement because
the use of transplants or plant seedlings
allows us to quantify easily the amount
of replanting that has occurred and
thereby ensure compliance with the 80/
60 rule time-in-place requirements. By
contrast, if an operator used seeding for
replanting, because of the variability in
seed germination it would be extremely
difficult to quantify the number of trees
and shrubs that would result from the
supplemental seeding. This would make
verification of compliance with the 80/
60 rule time-in-place requirements
extremely difficult, if not impossible.
The 80/60 rule time-in-place
requirements can be met when the
following easily documented facts are
established: (1) The final field count of
plants of approved species at bond
release shows that the requisite number
of plants are in place; (2) records show
that no woody species have been
planted in the last three years of a fiveyear responsibility period or six years of
a ten-year responsibility period; (3) if
replanting has occurred in the last 60
percent of the responsibility period,
planting records show that the number
of plants replanted is below 20 percent
of the final plant count; and (4) no
woody species have been planted
during the last two years of the
responsibility period. By establishing
these facts, it will now be possible for
an operator to make a numerical
assessment of compliance with the 80/
60 rule that is at least as accurate as
could be obtained under the current
laborious practice of having to
determine the length of time that
individual plants have been in place.
The second revision to
§ 816.116(b)(3)(ii), represented by the
third and fourth sentences added to the
end of existing rule language, will allow
volunteer plants of approved species to
be included in the 80/60 revegetation
success count even when it cannot be
verified that the volunteers are more
than two years old. Operators and
regulatory officials from both the humid
and semi-arid precipitation areas have
often questioned the wisdom of not
being able to include volunteer plants of
approved species in the 80/60
revegetation success count when it
cannot be verified that the volunteer
plants have been in place for not less
than two growing seasons. We believe
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the new provision permitting operators
to count volunteer plants is consistent
with section 515(b)(19) of the Act,
which requires the operator to establish
vegetation that is ‘‘capable of selfregeneration and plant succession at
least equal in extent of cover to the
natural vegetation of the area.’’ The
volunteer plants allowed under this
revision represent either regeneration of
species already present on the reclaimed
area or invasion of native species from
adjacent undisturbed areas, which is
itself a strong indication of plant
succession. Live volunteer plants are as
likely to continue to grow and mature as
transplants of the same species that may
be little more than two years old.
Therefore, counting the first products of
plant regeneration or invasion is a clear
and reasonable indicator of successful
reclamation and an appropriate revision
to the 80/60 rule.
The third revision to
§ 816.116(b)(3)(ii), represented by the
fifth sentence added at the end of
existing rule language, will allow
individual suckers from shrubs to be
counted as volunteer plants under the
80/60 rule when it is evident that the
shrub community is vigorous and
expanding. As discussed in our
proposed rule, many of the planted or
seeded shrub species in semi-arid areas
undergo a continual process called
‘‘suckering’’ by which multiple new
aboveground stems are generated from
the initial plant. It is not possible,
however, to document the time in place
of these new suckers. Therefore, even
though the sucker plant community may
be vigorous and expanding, the
individual suckers could not be counted
under the prior rule for purposes of
meeting the 80/60 revegetation success
count. As is the case with other
volunteer plants, we believe that
allowing for the counting of individual
suckers within a vigorous and
expanding shrub community is also a
reasonable indicator of successful
reclamation and an appropriate revision
to the 80/60 rule.
What were the comments submitted on
proposed revisions to
§ 816.116(b)(3)(ii)?
Fourteen commenters supported the
proposed revisions to § 816.116(b)(3)(ii)
and the new ways operators may
accurately establish compliance with
the 80/60 revegetation requirements of
that rule. These commenters echoed
many of the same themes that we had
set forth in our preamble to the
proposed rule. The commenters
affirmed that the new language added to
§ 816.116(b)(3)(ii) would reduce some of
the sampling problems and unnecessary
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burdens associated with proving
reclamation success on woodland land
uses. They viewed the new ability to
include volunteer trees and shrubs,
including suckers, in success
determinations as encouraging greater
use of woody species and the
reforestation of mined lands. Finally,
because the regenerative capabilities of
a planting can greatly increase its
prospects for long term success, they
confirmed that volunteer plants would
be no less valuable for determining
revegetation success than original
plantings.
One of the commenters supporting the
proposed revisions provided much
useful information for evaluating shrubs
from different shrub populations and
developing species-specific sampling
techniques. We particularly appreciate
this commenter’s insight into evaluating
shrubs. The provided information may
well prove useful in the future for
developing sampling techniques based
on the particular species of shrubs to be
sampled.
One commenter, however, objected to
the revision of § 816.116(b)(3)(ii) on the
grounds that it eliminated the
continuing need under the 80/60 rule to
make a plant count of trees and shrubs
for establishing revegetation success.
This commenter also expressed concern
that one-year-old suckers in the West
might be included in the final field
count, even though such suckers are not
viable. The commenter did not object to
counting suckers if they are vigorous
and expanding but observed that a
competent horticulturist or agronomist
familiar with an area should be able to
determine if a sucker ‘‘is going into its
second growing season.’’
We note that our revision of the
methods by which trees and shrubs can
be counted under the 80/60 rule does
not change the requirement that, during
the final year of the responsibility
period, the operator must still
demonstrate that the revegetation
success standard has been achieved.
This demonstration will require
sampling, i.e., field counting, the
individual trees and/or shrubs on the
reclaimed area. The counting of oneyear-old suckers should not be a
concern because, since they receive
nourishment from both the parent plant
and their own root system, their
continued survival and expansion
beyond year one should be reasonably
ensured. Evaluation of tree and shrub
density in the last year of the
responsibility period should also ensure
that the stands are well established.
Accordingly no changes are necessary to
address this commenter’s concern.
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Still another commenter opposed the
proposed revisions to the 80/60 rule
because it feared these revisions would
weaken the regulatory authority’s ability
to require success standards and
sampling techniques that would ensure
good and lasting reclamation. This
commenter stated that under the
proposed rule operators could
essentially choose whatever sampling
technique is least costly—whether the
technique is valid or not—and apply
reclamation performance standards as
they see fit. The commenter further
questioned how regulators and the
public would be able to hold operators
to a high and successful reclamation
standard. The commenter suggested
that, under the proposed rule, lands
might be released from reclamation
bonds even though they did not, in fact,
‘‘meet long lasting reclamation
requirements or the intent of the
SMCRA.’’
Contrary to this commenter’s
contention, our revisions to
§ 816.116(b)(3)(ii) will not weaken or
otherwise adversely affect the regulatory
authority’s ability to require that, during
the final year of the responsibility
period, the operator must still
demonstrate that the revegetation
success standard has been achieved. As
always, this demonstration under
§ 816.116(b)(3) will require sampling,
i.e., field counting, the tree and/or shrub
density on the reclaimed area and
comparing those counts to records of
original planting and replanting to
determine if revegetation is successful.
Under § 816.116(a)(1), the regulatory
authority will continue to select the
success standards and statistically valid
sampling techniques that operators must
use to demonstrate revegetation success.
Accordingly, the new methodologies
allowed under revised § 816.116(b)(3)(ii)
for establishing compliance with the
revegetation requirements of the 80/60
rule will not affect the quality of the
reclamation required under the Act.
These new methodologies will merely
allow the operator to demonstrate
achievement of the revegetation success
standard without having to track the
time in place of individual plants
through the revegetation responsibility
period.
6. Section 816.116(c)(3)(i) and (ii):
Sampling Timeframes for Areas With
Less Than 26 Inches of Precipitation
What are the revisions to
§ 816.116(c)(3)(i) and (ii)?
We have revised § 816.116(c)(3) to
change the timeframes for sampling
revegetated lands in areas receiving less
than 26 inches of precipitation to
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51699
determine if they meet the appropriate
success standards. Revised
§ 816.116(c)(3)(i) and (ii) will read as
follows, with new language in italics:
(i) Ten full years, except as provided in
paragraph (c)(3)(ii) below. The vegetation
parameters identified in paragraph (b) of this
section for grazing land, pasture land, or
cropland shall equal or exceed the approved
success standard during the growing season
of any two years after year six of the
responsibility period. Areas approved for the
other uses identified in paragraph (b) of this
section shall equal or exceed the applicable
success standard during the growing season
of the last year of the responsibility period.
(ii) Five full years for lands eligible for
remining included in permits issued before
September 30, 2004, or any renewals thereof.
To the extent that the success standards are
established by paragraph (b)(5) of this
section, the lands shall equal or exceed the
standards during the growing season of the
last year of the responsibility period.
This revised language is identical to
that included in the 2005 proposed rule.
We are changing our revegetation
regulations at § 816.116(c)(3) to bring
the timing of revegetation success
measurements for areas of 26 inches or
less of average annual precipitation
(‘‘semi-arid areas’’) into line with those
for areas of greater than 26 inches of
average annual precipitation (‘‘humid
areas’’) at § 816.116(c)(2). As discussed
more fully in our 2005 proposed rule,
our 1979 regulations provided for the
timing of revegetation success
measurements for semi-arid areas to be
identical to that for humid areas. These
regulations required that the
revegetation success standards be
equaled or exceeded for the last two
consecutive years of the respective fiveand ten-year responsibility periods. In
1983, we revised our humid area
regulations, redesignated as
§ 816.116(c)(2)(i), to require that
revegetation success standards be
equaled or exceeded during the growing
season of the last year of the five-year
responsibility period, or, if required by
the regulatory authority, during the
growing season of the last two
consecutive years of responsibility
period. We did not, however, change the
semi-arid area regulation at
§ 816.116(c)(3)(i), which continued to
require that the revegetation success
standard be equaled or exceeded for the
last two consecutive years of the tenyear responsibility period. In 1985, the
court remanded the 1983 revision to us
because of the lack of supporting
evidence.
On September 7, 1988, we
promulgated the current rules at
§ 816.116(c)(2)(i) setting forth the
periods for measuring revegetation
success for humid areas with a five-year
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responsibility period. 53 FR 34643. The
new regulations required that
revegetation success standards for
grazing land, pasture land, or cropland
postmining land uses be equaled or
exceeded during any two years of the
responsibility period, except the first.
Prior to the 1988 revision to
§ 816.116(c)(2)(i), evaluation of
revegetation success was required in the
last two years of the responsibility
period for these land uses, regardless of
the precipitation regime. In support of
this relaxation from the 1979 ‘‘last-twoconsecutive-years-of-the-responsibilityperiod’’ standard, the 1988 preamble
noted that the earlier 1983 preamble had
cited the effect of year-to-year [climatic]
variability on crop yields or other
parameters that are highly sensitive to
such conditions as justifying the
requirement of two consecutive years of
revegetation success. 48 FR 40156,
September 2. Notwithstanding, we
reasoned that, relative to grazing land,
pasture land, and cropland postmining
land uses in humid areas,
‘‘[m]easurement in nonconsecutive
years avoids unduly penalizing the
operator for the negative effects of
climatic variability.’’ The 1988 preamble
continued, ‘‘OSM * * * believe[s] that
measurement over two years is
important to attenuate the influences of
climatic variability, but now realizes
that consecutiveness imposes an
unnecessary degree of regulatory
rigidity.’’ Furthermore, we argued that
to require measurement of crop or
pasture yields in the last year of the
responsibility period would be an
unnecessarily rigid standard given the
variability of weather conditions. 53 FR
34640.
The 1988 revision also provided that,
for humid areas, the revegetation
success standards for postmining land
uses other than grazing land, pasture
land, and cropland, e.g., forest products,
fish and wildlife habitat, etc., must be
equaled or exceeded during the growing
season of the last year of the
responsibility period. Supporting this
relaxation of the 1979 ‘‘last-twoconsecutive-years-of-the-responsibilitystandard,’’ we reasoned that within a
forest ecosystem there exists a positive
relationship between time and
vegetative cover. Therefore, we
concluded that, for forest-type
ecosystems, the last year of the
responsibility period would provide an
accurate measurement of revegetation
success. 53 FR 34641.
After reviewing the 1988 preamble
rationale that supported relaxation of
the last-two-consecutive-years
requirement for humid areas with a fiveyear responsibility period, we have not
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found any persuasive reason why the
same rationale would not equally apply
to semi-arid areas with a ten-year
responsibility period. For example, for
areas with postmining land uses other
than grazing land, pasture land, or
cropland, determining vegetation
success requires measurement of
vegetative parameters that are not
sensitive to short-term weather
variations. With each of these other
postmining land uses, the vegetative
measurements done for the last year of
the responsibility period can be
reasonably expected to represent the
baseline for vegetative success in future
years. Trees counted in the last year of
the responsibility period for a forestry
postmining land use should reasonably
be expected to survive as a permanent
vegetative cover. This holds true
whether the other postmining land uses
are located in humid or semi-arid areas.
For all postmining land uses, we believe
that it is the nature of the individual
postmining land use and not the relative
moisture of the area in which the land
use is located that appropriately
determines the number and spacing of
the years for which vegetation success
must be measured.
Accordingly, we have revised our
regulations for semi-arid areas at
§ 816.116(c)(3)(i) to comport with our
regulations for humid areas at
§ 816.116(c)(2)(i). The revised rules for
semi-arid areas provide that the
vegetation parameters identified in
§ 816.116(b) for grazing land, pasture
land, or cropland must equal or exceed
the approved success standard during
the growing season of any two years
after year six of the responsibility
period. For semi-arid areas approved for
the other land uses identified in
paragraph (b) of that section, vegetation
must equal or exceed the applicable
success standard during the growing
season of the last year of the
responsibility period.
Revising the revegetation rules in this
manner makes the requirements of
§ 816.116(c)(3)(i) for areas receiving 26
inches or less of annual precipitation
similar to those of § 816.116(c)(2)(i) for
areas receiving more than 26 inches of
annual precipitation. For the sake of
further consistency, we are similarly
revising the rules for lands in semi-arid
areas at § 816.116(c)(3)(ii), which govern
the timing of revegetation success
measurement for lands eligible for
remining, to comport with the rules for
similar lands in humid areas at
§ 816.116(c)(2)(ii). Both rules will then
require that revegetation standards be
met or exceeded during the growing
season of the last year of responsibility
period.
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What were the comments submitted on
proposed revision to § 816.116(c)(3)?
Nine commenters supported the
proposed revision that would require
revegetation success measurements for
grazing land, pasture land, and cropland
in semi-arid areas to equal or exceed the
approved success standard during the
growing season for any two years after
year six of the ten-year responsibility
period. Noting that our 1988 rulemaking
had cited the climatic variability of
humid areas as supporting the new anytwo-year measurement schedule for
grazing lands, pasture lands, and
croplands, commenters added that the
climatic variability in the semi-arid
areas of the West can also be very
extreme, particularly with regard to
periods of drought. Because vegetation
parameters may equal or exceed success
standards in the years both before and
following a drought, commenters
concluded that flexibility was needed to
allow the second year of sampling to be
collected in a non-consecutive year.
Accordingly, with regard to grazing
lands, pasture lands, and croplands in
semi-arid areas, commenters supported
the proposed rule as allowing needed
flexibility in the timing of revegetation
success measurements without
compromising the standard for that
success.
We agree with this analysis. By
allowing measurements for revegetation
success in any two years after year six
of the responsibility period, the new
rule will provide semi-arid areas with
the same flexibility for dealing with
climatic variability presently afforded
only in humid areas. At the same time
both rules will ensure not only
successful revegetation, but also timely
bond release.
One commenter noted that if an
operator is using a reference area as the
success standard against which
revegetated areas will be compared, the
climatic variability discussed in the
preamble would not pose substantial
problems during bond release
demonstrations because the reference
area would be subject to the same
climatic variability as the revegetated
area.
We generally agree with this
comment, noting that if reference areas
are located in close proximity to
revegetated areas, the amount of
climatic variability between any two
areas may not be substantial. However,
as mines expand, the distances between
long-established reference areas and
newly reclaimed areas often increase.
Given the localized nature of storms in
the West, these increased distances can
result in increased climatic variability
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between the reference and revegetated
areas. Therefore, we believe that it is
particularly important to take into
account the potential for climatic
variability between reference and
revegetated areas when the two are not
in close proximity.
Another commenter opposed revising
the measurement time frames for
grazing land, pasture land, and cropland
in semi-arid areas to comport with those
in humid areas. Because the climate of
the area determines the specific plants
used to achieve approved postmining
land uses, this commenter declared that
it is entirely possible to plant for a
specified land use and then, due to
changed climatic conditions, fail to
meet the revegetation standards in any
year of the ten-year responsibility
period. For example the commenter
indicated that in May 1996, she had
planted a dry land hay field of grass and
legume mix on undisturbed soils. In the
nine subsequent years, she harvested
only one crop and that crop was only
half a crop. Because climate determined
the production on that hay field, not her
intention to use the land as a hay field,
she did not think that picking any two
years out of the last four years of the
ten-year responsibility period is either a
conservative or safe way to determine
the ultimate survivability of semi-arid
western vegetation. She reasoned that, if
the vegetation meets the standards for
the last two years, then there would be
a better probability that the reclaimed
area would be able to meet the intended
postmining land use. In this context, the
commenter also stated that drought and
wet cycles in the West alternate on
much longer time frames than those in
the East. The commenter further
suggested that OSM could extrapolate
the duration of the past drought cycles
from available information, noting that
some of these drought cycles were
reputed to have lasted for extended
periods. On this basis, the commenter
concluded that OSM should err on the
side of caution and retain the current
rule.
We do not agree with many of the
conclusions expressed by this
commenter. Meeting the success
standards for pasture land, grazing land
or cropland in the last two years of the
ten-year responsibility period is not
necessarily a better indicator of
revegetation success than meeting the
same success standards in any two years
after year six. For example, suppose an
operator in a semi-arid area were to
meet grassland production and cover
success standards in year seven, but,
because of drought, did not meet those
same success standards in years eight
and nine. Then, because precipitation
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returned to normal in year ten, the
operator met the grassland production
and cover success standards in that
year, thus satisfying the new standard of
any two years of the responsibility
period after year six. We believe that
this any-two-year approach clearly
demonstrates the permanence,
resilience and effectiveness of the
reclaimed plant community following a
period of drought. Such a clear
demonstration of the resilience of the
reclaimed plant community would not,
however, satisfy the evaluation time
frames of the prior rule when the data
could only be collected in the last two
consecutive years of the responsibility
period. In the commenter’s personal
example of the dry land hay field, the
hay field would not have met either the
prior standard supported by the
commenter or the new standard
finalized in this rulemaking. We note
that, if there are concerns as to the
adequacy of revegetation at the time of
the bond release inspection, the
regulatory authority should conduct
additional vegetation investigations.
Another commenter had two other
concerns with our proposed revisions to
the time frames for measuring
revegetation success in semi-arid areas
with grazing land, pasture land, or
cropland postmining land uses. First, he
asserted that the proposed language
would allow the first year of
measurement for grazing land, pasture
land, and cropland to be conducted in
the seventh year after the last
augmented seeding. The commenter
found this fact particularly troubling as,
in the semi-arid areas of the West, the
reclaimed vegetation community in year
seven is still undergoing significant
changes in composition, cover, and
production. The commenter’s second
concern was that the proposed rules
would sometimes allow a demonstration
of revegetation success many years
before an operator requests formal bond
release. More specifically, an operator
could conceivably demonstrate that he
had met revegetation success in years
seven and eight but not apply for formal
bond release until year twenty.
Accordingly, the commenter suggested
that we change the rules to require
measurement of revegetation success in
two out of the last three years of the
responsibility period. The commenter
viewed this suggested change as tying
the demonstration of revegetation
success to the formal bond release
request while still allowing flexibility in
addressing negative impacts to the
reclamation caused by climatic
variability.
We agree that reclaimed plant
communities are dynamic and change
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over time as the plants mature and
composition responds to climatic
variability and soil conditions.
However, this change within plant
communities will also continue long
after the responsibility period is over.
Therefore, OSM does not believe that
the fact of continuing change within
plant communities is sufficient reason
to delay measurement of revegetation
success on grazing land, until either the
last two years of the responsibility
period, as the rule formerly provided, or
two out of the last three years of the
responsibility period as this commenter
suggested. Pasture land and cropland
are not subject to significant change in
composition, cover and/or production
over time because of the nature of the
plant species planted. Once established,
cover and/or production on these land
uses generally fluctuates only in
response to climatic variability. For
these reasons we revised the rule to
allow measuring for revegetation
success on grazing land, pasture land,
and cropland in any two years after year
six. We find it unlikely that an operator
might measure revegetation success in
years seven and eight but wait until year
twenty to request bond release. Even so,
§ 800.40(c)(3) clearly requires that the
operator must fully meet the
requirements of the Act and the permit
(including revegetation success
standards) for a phase III bond release.
Therefore, if, the regulatory authority is
concerned that vegetation does not meet
the revegetation success standards
during the final bond release inspection,
the regulatory authority can and should
require additional investigation to
determine whether those standards have
been met. The regulatory authority may
also set limitations on acceptable
timeframes for sampling vegetation
prior to submission of a bond release
application. Accordingly, no change in
the regulation is necessary to address
the commenter’s concern.
While five commenters agreed with
the proposed revision to
§ 816.116(3)(c)(i) as it applied to pasture
land, grazing land, and cropland in
semi-arid areas, they did not agree with
the revision as it applied to the semiarid areas approved for the ‘‘other uses’’
identified in § 816.116(b)(3), (4) and (5).
Under the proposed revision, identified
vegetative parameters in semi-arid areas
would have to meet or exceed the
applicable success standard during the
growing season of the last year of the
responsibility period. These
commenters asserted that this particular
revision would be overly burdensome to
operators who, in some situations,
would have to conduct a total of three
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separate samplings of the vegetation in
a large tract with mixed land uses to
qualify for bond release. In contrast,
commenters asserted that the prior rule
would only require two samplings of
vegetation in same large tract to qualify
for bond release. The commenters
characterized the additional sampling
required under the proposed rule as an
unnecessary expenditure of time and
money. To alleviate this problem the
commenters proposed to allow
revegetation sampling for the other land
uses of § 816.116(b) in any one year after
year six of the responsibility period.
This proposed change would, for large
tracts with mixed land uses, allow
operators to reduce their sampling
efforts to two years by sampling for the
other uses in the same year as they
sample for grazing land, pasture land, or
cropland.
As a supporting example of the
asserted sampling burden of our
proposed rule, the commenters noted
that many western surface coal mines
reclaim mined lands to multiple land
uses. Operators may reclaim large
portions of a reclaimed area to a grazing
land postmining land use dominated by
forage plants, while other smaller
portions of the same area may be
reclaimed to a different postmining land
use, such as fish and wildlife habitat
dominated by woody plants. The
resultant landscape would be a mosaic
of grass-dominated plant communities,
subject to the frequency of success
determinations for grazing land,
intermixed with shrub-dominated
communities, and subject to the
frequency of success determinations for
fish and wildlife habitat. Commenters
accurately noted that, to demonstrate
revegetation success under the proposed
rule, operators could choose to sample
the grazing lands to demonstrate
revegetation success in any two years of
years seven, eight, nine, or ten of the
responsibility period. However,
operators would have to sample fish and
wildlife habitat in year ten, the last year
of the responsibility period. Thus, they
concluded, sampling within the mosaic
of a large reclaimed area would have to
occur on three different occasions.
In further support of their proposal to
allow revegetation sampling in any year
after year six of the responsibility
period, these commenters also indicated
that operators must sample woody plant
density on an interim, ongoing basis to
assure that augmented plantings are
made in a timely fashion. Otherwise
operators would risk the restarting of
their liability period because they might
have waited too long before determining
that a stand of woody plants would not
meet the density standard applicable to
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woody plants. While the commenters
acknowledged that interim vegetation
sampling could properly be used under
their proposal to demonstrate
achievement of the success standard
without the need for augmented
planting, the commenters stressed that
operators would still have to resample
the same stand in the last year of the
responsibility period to demonstrate
revegetation success under revised
§ 816.116(c)(3). Commenters stated that,
in their experience, if interim vegetation
monitoring confirms the operator has
established appropriate woody plant
density and has met the revegetation
success standard prior to year ten, the
woody plant density will be the same or
better in year ten. The regulatory
authority could also confirm the
required woody plant density at the
mandatory qualitative final field
inspection for bond release.
Accordingly, the commenters proposed
revising the language of
§ 816.116(c)(3)(i) to allow operators to
sample revegetation for areas approved
for other uses identified in
§ 816.116(b)(3), (4), and (5) in any one
year after year six of the responsibility
period. These commenters maintained
that this suggested change would also
encourage diversity of both species and
land uses on reclaimed lands.
Still another commenter concluded
that there was no benefit to delaying
measurement of revegetation success for
the other land uses identified in
§ 816.116(b)(3), (4) and (5) until the last
year of the responsibility period. This
commenter indicated that its conclusion
was supported by the same rationale
that OSM had used in its 2005 preamble
to justify proposing reduction of the
evaluation period for these other land
uses from the last two years to the final
year of the responsibility period. For
example, the commenter reasoned that
once woody plants are established, their
density and cover is not highly variable
from year to year as they are not
sensitive to short-term weather
variations. Forest-related ecosystems
may therefore be expected to improve as
they mature since a positive
relationship exists between time and
vegetative cover. Furthermore, whatever
the year during which a land use
involving woody plants meets its
required success standards, the
regulatory authority will have to inspect
that land again at bond release to ensure
that the land use is still functioning as
intended. In addition to there being no
perceived benefit to delaying the
measurement of revegetation success
required by § 816.116(c)(3) until the last
year of the responsibility period, the
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commenter stated that the inconsistent
timing requirements for measuring the
revegetation success of both grazing
land, pasture land, cropland and other
land uses may further cause an added
and unnecessary burden for measuring
vegetation in large areas. The other land
uses identified in § 816.116(b)(3), (4),
and (5) often constitute only a small
proportion of larger surrounding tracts
devoted to grazing, pasture or cropland.
For example, grazing tracts often
include interior wetlands and
woodlands. While these grazing tracts
could have been measured in any two
years after year six of the responsibility
period under OSM’s proposed rule,
wetlands and woodlands, as other land
uses, could only be measured in the
final year of the responsibility period.
Therefore, to make the timing of success
measurements consistent for all land
uses, to reduce the burden of measuring
in different years for several uses in the
same inclusive bond release tract, and
because of the lack of annual variability
in woody plant cover, the commenter
recommended that ‘‘the-growing-seasonof-the-last-year’’ provision be struck
from the proposed regulation. By this
proposal, we understand the commenter
to be also proposing that OSM amend
§ 816.116(c)(3)(i) to allow sampling of
revegetation success on semi-arid areas
with the other uses identified in
§ 816.116(b)(3), (4), and (5) in any year
after year six of the responsibility
period.
We do not accept these commenters’
proposal. As discussed in our 2005
Federal Register notice, we proposed to
amend § 816.116(c)(3)(i) to make the
sampling timeframes for measurement
of revegetation success in semi-arid
areas consistent with the requirements
of § 816.116(c)(2). Section 816.116(c)(2),
governing humid areas, continues to
require evaluation of revegetation
success for land uses other than pasture
land, grazing land or cropland in the
last year of the responsibility period.
The 1988 revision of § 816.116(c)(2)
provided that, for humid areas, the
revegetation success standards for
postmining land uses other than grazing
land, pasture land, and cropland be
equaled or exceeded during the growing
season of the last year of the
responsibility period. Supporting this
revision, which was a relaxation of the
prior standard adopted in 1979 (‘‘last
two consecutive years of the
responsibility period’’), we reasoned
that, in a forest ecosystem, a positive
relationship exists between time and
vegetative cover. Therefore, we
concluded that, for forest ecosystems,
the last year of the responsibility period
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would provide an accurate
measurement of revegetation success. 53
FR 34641. While forest ecosystems may
develop at slower rates in semi-arid
areas, in both humid and semi-arid
areas a positive relationship exists
between time and vegetative cover. And
while we did not specifically discuss
the matter in the 1988 preamble, the
same positive relationship between time
and vegetative cover exists for shrub
land ecosystems in both humid and
semi-arid areas. Consequently, for both
areas, the last year of the responsibility
period would be the best time to
accurately measure revegetation
success. For the reasons discussed
above, we believe that the most
appropriate time to evaluate
revegetation success for forest and shrub
lands in semi-arid areas is during the
last year of the responsibility period. We
are retaining the proposed changes to
§ 816.116(c)(3) in our final rule.
We further believe that the
commenters who gave the example
involving the measurement of
revegetation success for a large tract
with mixed land uses miscalculated the
number of sampling events required of
each land use for bond release under
our prior rule. While that rule would
have required the sampling of
vegetation in the same two years for a
large tract with mixed land uses, the
total number of required sampling
events for those two years would be a
minimum of four—two sampling events
for grazing land, etc., and two for any
of the other land uses of § 816.116(b).
Commenters were correct that our
proposed revision to § 816.116(c)(3)(i)
might require a total of three years of
sampling for a large tract with mixed
land uses. The proposed revision
would, however, for these other land
uses reduce the number of years that
operators must measure revegetation
success from two to one years. This
constitutes a 50 percent reduction in the
operators’ sampling burden. This
burden is not significant as is suggested
by one comment stating that some
operators voluntarily monitor woody
plant stocking on an ongoing basis and
do not consider the monitoring to be
burdensome. And the commenters are
incorrect in their suggestion that the
only way they could limit their
sampling effort to two years would be to
sample in years nine and ten. Under the
revised rule, an operator conducts the
first sampling event in either years
seven, eight, or nine for grazing land
and then, in year ten, conducts the
second sampling event for grazing land
and the only sampling event for fish and
wildlife habitat. Finally, commenters
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provided no information supporting
their assertion that allowing
measurement of revegetation success
during any year after year six would
encourage both land use and species
diversity on reclaimed lands. Nor do we
have any reason to believe that our
revision to § 816.116(c)(3) will adversely
affect land use or species diversity, as
our prior regulation at § 816.116(c)(3)
also required sampling during the last
year of the responsibility period.
In sum, we believe that the new
requirement that operators must
conduct evaluation of revegetation
success for the other land uses
identified in § 816.116(b) during the last
year is not overly burdensome and will
ensure national consistency in
evaluating revegetation success for these
other uses both in humid and semi-arid
areas.
Other Comments
Although we did not propose any
revisions to the timeframes of
§ 816.116(c)(2) that govern the sampling
for revegetation success in humid areas,
ten commenters proposed eliminating
the current provision of
§ 816.116(c)(2)(i) that prohibits
sampling in the first year of the
responsibility period. These
commenters based this proposal on their
longstanding experience in evaluating
revegetation efforts and their belief that
such a change would allow operators in
some States the opportunity to earlier
achieve both phase II and phase III bond
release. The commenters asserted that
the past twenty years of SMCRA
reclamation had resulted in a general
consensus in the Midwest that the first
year of reclamation is the most difficult
in terms of successfully meeting
required target yields. Citing their
various discussions over the years with
State and Federal regulatory personnel,
academia, consultants and operators,
the commenters knew no sound reason
for not measuring revegetation success
in the first year. These commenters did
note that the preamble in the September
7, 1988, Federal Register suggests that
a beneficial fertilization carryover effect
from initial seeding may produce
inaccurate results in the first year.
However, the same preamble discussion
also concludes that any carry-over effect
from the initial fertilization would be
insignificant when compared to normal
annual fertilization practices.
Accordingly, the commenters concluded
that the first-year exception is
unnecessary. They asserted that
allowing the first year to be used for
proof of productivity for pasture land,
grazing land, and cropland would allow
operators the opportunity in some States
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51703
to more quickly achieve both phase II
and phase III bond release. In light of
what they perceived as the current
difficulty in obtaining surety bonds in
the mining industry, the commenters
suggested that earlier bond release
would provide significant relief in
obtaining surety bonds. Also, the
commenters maintained that the
opportunity for earlier proof of
productivity and bond release would
provide operators an incentive to
improve their methods of handling
soils.
We appreciate the interest expressed
by these commenters in proposing that
we revise the provision in
§ 816.116(c)(2)(i) that prohibits
measuring vegetation in the first year of
the responsibility period for humid
areas. However, we did not consider
this revision in our 2005 proposed rule,
and it falls far beyond the scope of the
current rulemaking. To include it in the
current rulemaking would necessitate a
reopening of the comment period on the
proposed rule resulting in further delay
in implementing its proposed changes.
For this reason, we are not accepting the
commenters’ proposal at this time. We
will, however, take the proposal under
advisement and may include it in a
future rulemaking.
Nonetheless, we would like to take
this opportunity to address apparent
confusion in some of the comments
supporting this suggested change to
§ 816.116(c)(2)(i). Several of these
comments suggested that revising
§ 816.116(c)(2)(i) to allow evaluation of
revegetation success for pasture land,
grazing land, and cropland in the first
year would allow operators in some
States to earlier achieve both phase II
and Phase III bond release. In fact,
allowing evaluation of revegetation
success for pasture land, grazing land,
and cropland in the first year would not
affect when either phase II or III bond
release could occur. The Federal
regulations governing standards for
success in § 816.116, including
§ 816.116(c)(2)(i), do not apply to phase
II bond release. For the land uses
covered by § 816.116(c)(2)(i),
§ 800.40(c)(2) allows phase II bond
release to be granted when topsoil has
been redistributed (if it is not included
as part of a phase I bond release), and
vegetation is established. There is no
regulatory requirement to meet cover or
production standards for a phase II bond
release. Therefore, allowing
measurement of cover and production
in the first year has no effect on when
a phase II bond release can occur. In
turn, phase III bond release cannot be
granted sooner than five years after the
last augmented seeding or planting,
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regardless of when measurement occurs.
Under the current Federal regulations,
the operator then has four years prior to
the end of the five year responsibility
period to conduct revegetation sampling
and demonstrate revegetation success.
Therefore, even if we did allow
measurement of cover and production
in the first year after the last augmented
seeding as the commenters proposed,
the period of responsibility for phase III
bond release would still last five years
from the last augmented seeding.
Two commenters also suggested that
we develop incentives to use the five
forestry reclamation techniques
recommended by the Appalachian
Regional Reforestation Initiative (ARRI)
in its recent reforestation brochure.
These commenters warned that we need
additional initiatives to encourage
reforestation efforts, and indicated that
there has been extensive research
conducted on how to better reforest
reclaimed mined land. Contrasting the
leading role that ARRI has taken in
promoting enhanced reforestation
techniques that are based on this
research, the commenters emphasized
that regulatory requirements have too
often acted as a disincentive for
operators’ selecting forestry as a
postmining land use.
In response to this comment, we
recognize that forest fragmentation and
the reduction of biodiversity are valid
concerns and have endeavored to
address them in several ways. The
current revisions to the regulations
governing topsoil replacement and
revegetation would, among other things,
encourage species diversity and remove
an impediment to the reforestation of
reclaimed land. In addition, our agency
took the lead in establishing the ARRI
for the purpose of restoring forests on
lands disturbed by coal mining
operations in the eastern United States.
ARRI is a coalition of diverse groups
comprised of OSM and State
government agencies that regulate coal
mining in Kentucky, Maryland, Ohio,
Pennsylvania, Tennessee, Virginia, and
West Virginia. It advocates a specific
forestry reclamation approach that,
when implemented properly, can
provide significant cost savings to mine
operators while providing for greater
survival and productivity of planted
trees, enhancing natural succession, and
reducing erosion, sedimentation, and
downstream flooding. The industry, the
environmental community, landowners,
academics, and other governmental
agencies have recognized these benefits.
At the present time, however, it is
unclear what additional incentives
might be appropriate to promote the
reforestation of mined lands. Interested
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parties can access information about
ARRI on the Internet at https://
arri.osmre.gov/PDFs/ARRI.brochure.pdf.
We received one final comment that
questioned the appropriateness of using
‘‘ground cover,’’ as defined in the
Federal regulations at § 701.5, instead of
using perennial vegetative cover for
evaluating revegetation success under
§ 816.116(a)(2). The commenter further
opposed including annual species and
litter (dead plant material) in
evaluations of ground cover, as is
allowed under the current Federal
definition of ‘‘ground cover,’’ and
contended that revegetation success
evaluations should focus on the cover of
perennial species.
We had not proposed revising the
definition of ‘‘ground cover’’ because
that definition was not identified as an
issue either during prior revegetation
outreach efforts or consultations with
regulatory authorities. However, should
a regulatory authority propose revising
its definition of ‘‘ground cover’’ to
include only vegetative cover or
perennial cover and demonstrate that
the new definition is no less effective
than the Federal definition in
implementing the requirements of
SMCRA, we would approve the use of
such a definition.
What effect will this rule have on
approved State programs, on Federal
programs, and on Indian lands?
Following publication of the final
rule, we will evaluate the State
programs approved under section 503 of
SMCRA and 30 CFR part 732 to
determine if any changes in those
programs are necessary to maintain
consistency with Federal requirements.
When we determine that a State
program should be amended, we will
notify the State in accordance with the
provisions of § 732.17(d).
We have made a preliminary
determination to require that State
programs with provisions authorizing
undeveloped land as a postmining land
use adopt success standards for
undeveloped land as required by
§§ 816.116(b)(3) and 817.116(b)(3). We
have also made a preliminary
determination that, with regard to the
other provisions in the final rule, States
may adopt similar provisions if they
choose to, but will not be required to
amend their programs.
Through cross-referencing, this final
rule applies to all lands in States with
Federal regulatory programs. States with
Federal regulatory programs include
Arizona, California, Georgia, Idaho,
Massachusetts, Michigan, North
Carolina, Oregon, Rhode Island, South
Dakota, Tennessee and Washington.
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Those programs are codified at 30 CFR
parts 903, 905, 910, 912, 921, 922, 933,
937, 939, 941, 942, and 947,
respectively.
The revisions to 30 CFR parts 816 and
817 apply to Indian lands as a result of
the cross-referencing in § 750.16.
III. Procedural Matters and Required
Determinations for This Rule
Executive Order 12866—Regulatory
Planning and Review
This document is considered a
significant rule and is subject to review
by the Office of Management and
Budget (OMB) under Executive Order
12866.
a. This rule will not have an effect of
$100 million or more on the economy.
It will not adversely affect in a material
way the economy, productivity,
competition, jobs, the environment,
public health or safety, or State, Tribal,
or local governments or communities.
The revisions to the regulations
governing topsoil redistribution and
revegetation success standards will not
have an adverse economic impact on the
coal industry or State regulatory
authorities. During any given year,
approximately 880 operators conduct
vegetation sampling for bond release.
The revisions may reduce operating
expenses for coal operators by reducing
the time needed to conduct revegetation
evaluations and obtain bond release.
The estimated reduction in costs is
nonquantifiable.
We estimate that approximately two
State regulatory authorities will modify
their standards for revegetation success
during a year, requiring approximately
100 hours to complete each
modification. Under the rule, however,
the estimated savings will be limited to
the costs of submitting the proposed
modification to OSM for approval as
required by §§ 816.116(a)(1) and
817.116(a)(1) prior to revision. Those
costs usually include the expense
involved in preparing a transmittal
letter and the costs of transmission to
OSM.
The principal savings to the Federal
government will result from the
elimination of the need to draft, review,
approve, and publish a proposed rule
announcing receipt of, and seeking
comment on the modification, and the
need to draft, review, approve, and
publish a final rule announcing OSM’s
decision on the State submitted
modification. We estimate total annual
savings of approximately $10,000–
$12,000 per year. This estimate is based
on the cost of drafting, reviewing, and
approving two proposed and two final
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rules and the publication cost of $465
per page in the Federal Register.
b. This rule will not create a serious
inconsistency or otherwise interfere
with an action taken or planned by
another agency.
c. This rule does not alter the
budgetary effects of entitlements, grants,
user fees, or loan programs or the rights
or obligations of their recipients.
d. The proposed revisions to our
topsoil redistribution and revegetation
success standards may raise novel legal
or policy issues, which is why the rule
is considered significant by OMB under
Executive Order 12866.
Executive Order 13211—Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not considered a
significant energy action under
Executive Order 13211. The proposed
revisions to our regulations that govern
topsoil redistribution and revegetation
success standards notice will not have
a significant affect on the supply,
distribution, or use of energy.
Regulatory Flexibility Act
The Department of the Interior
certifies that this rule will not have a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.). As previously
discussed, some of the revisions may
facilitate bond release resulting in a
reduction in operating costs for coal
operators. Further, the rule produces no
adverse effects on competition,
employment, investment, productivity,
innovation, or the ability of United
States enterprises to compete with
foreign-based enterprises in domestic or
export markets.
jlentini on PROD1PC65 with RULES2
Small Business Regulatory Enforcement
Fairness Act
This rule is not a major rule under 5
U.S.C. 804(2), the Small Business
Regulatory Enforcement Fairness Act.
For the reasons previously stated, this
rule:
a. Does not have an annual effect on
the economy of $100 million or more.
b. Will not cause a major increase in
costs or prices for consumers,
individual industries, Federal, State, or
local government agencies, or
geographic regions.
c. Does 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
for the reasons stated above.
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16:49 Aug 29, 2006
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51705
Unfunded Mandates Reform Act
This rule does not impose an
unfunded mandate on State, Tribal, or
local governments or the private sector
of more than $100 million per year. The
rule does not have a significant or
unique effect on State, Tribal, or local
governments or the private sector. A
statement containing the information
required by the Unfunded Mandates
Reform Act (2 U.S.C. 1531 et seq.) is not
required.
that this rule will not significantly affect
the quality of the human environment
under section 102(2)(C) of the National
Environmental Policy Act of 1969
(NEPA), 42 U.S.C. 4332(2)(C). The EA
and finding of no significant impact are
on file in the OSM Administrative
Room, room 101, 1951 Constitution
Avenue, NW., Washington, DC 20240.
Executive Order 12630—Takings
The revisions to the regulations
governing topsoil redistribution and
revegetation success standards do not
have any significant takings
implications under Executive Order
12630. Therefore, a takings implication
assessment is not required.
Environmental protection, Reporting
and recordkeeping requirements,
Surface mining.
Executive Order 13132—Federalism
In accordance with Executive Order
13132, the rule does not have significant
Federalism implications to warrant the
preparation of a Federalism Assessment
for the reasons discussed above.
Executive Order 12988—Civil Justice
Reform
In accordance with Executive Order
12988, the Office of the Solicitor has
determined that this rule does not
unduly burden the judicial system and
meets the requirements of sections 3(a)
and 3(b)(2) of the Order.
Executive Order 13175—Consultation
and Coordination With Indian Tribal
Governments
In accordance with Executive Order
13175, we have evaluated the potential
effects of this rule on Federally
recognized Indian Tribes and have
determined that the proposed revisions
to our regulations that govern topsoil
redistribution and revegetation success
standards will not have substantial
direct effects on the relationship
between the Federal Government and
Indian Tribes, or on the distribution of
power and responsibilities between the
Federal Government and Indian Tribes.
Paperwork Reduction Act
We have determined that this rule
does not substantially alter the currently
approved collections of information
authorized by the Office of Management
and Budget under 44 U.S.C. 3501 et seq.
OMB has previously approved the
collection activities and assigned
clearance number 1029–0047 for 30 CFR
parts 816 and 817.
National Environmental Policy Act
OSM has prepared an environmental
assessment (EA) and has made a finding
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List of Subjects
30 CFR Part 816
30 CFR Part 817
Environmental protection, Reporting
and recordkeeping requirements,
Underground mining.
Dated: July 12, 2006.
R.M. ‘‘Johnnie’’ Burton,
Director, Minerals Management Service,
Exercising the delegated authority of the
Assistant Secretary, Land and Minerals
Management.
Accordingly, we are amending 30 CFR
parts 816 and 817 as set forth below.
I
PART 816—PERMANENT PROGRAM
PERFORMANCE STANDARDS—
SURFACE MINING ACTIVITIES
1. The authority citation for part 816
continues to read as follows:
I
Authority: 30 U.S.C. 1201 et seq.; and sec.
115 of Public Law 98–146.
2. In § 816.22, revise paragraphs (d)(1)
introductory text and (i) to read as
follows:
I
§ 816.22
Topsoil and subsoil.
*
*
*
*
*
(d) * * *
(1) Topsoil materials and topsoil
substitutes and supplements removed
under paragraphs (a) and (b) of this
section shall be redistributed in a
manner that—
(i) Achieves an approximately
uniform, stable thickness when
consistent with the approved
postmining land use, contours, and
surface-water drainage systems. Soil
thickness may also be varied to the
extent such variations help meet the
specific revegetation goals identified in
the permit;
*
*
*
*
*
I 3. Amend § 816.116 as follows:
I A. Revise paragraph (a)(1);
I B. Revise the first sentence of
paragraph (b)(3) introductory text;
I C. Add five sentences to the end of
paragraph (b)(3)(ii);
I D. Revise paragraphs (c)(3)(i) and (ii).
The revisions read as follows:
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§ 816.116
success.
Federal Register / Vol. 71, No. 168 / Wednesday, August 30, 2006 / Rules and Regulations
Revegetation: Standards for
jlentini on PROD1PC65 with RULES2
(a) * * *
(1) Standards for success and
statistically valid sampling techniques
for measuring success shall be selected
by the regulatory authority, described in
writing, and made available to the
public.
(b) * * *
*
*
*
*
*
(3) For areas to be developed for fish
and wildlife habitat, recreation,
undeveloped land, or forest products,
success of vegetation shall be
determined on the basis of tree and
shrub stocking and vegetative ground
cover. * * *
(i) * * *
(ii) * * * The requirements of this
section apply to trees and shrubs that
have been seeded or transplanted and
can be met when records of woody
vegetation planted show that no woody
plants were planted during the last two
growing seasons of the responsibility
period and, if any replanting of woody
plants took place during the
responsibility period, the total number
planted during the last 60 percent of
that period is less than 20 percent of the
total number of woody plants required.
Any replanting must be by means of
transplants to allow for adequate
accounting of plant stocking. This final
accounting may include volunteer trees
and shrubs of approved species.
Volunteer trees and shrubs of approved
species shall be deemed equivalent to
planted specimens two years of age or
older and can be counted towards
success. Suckers on shrubby vegetation
can be counted as volunteer plants
when it is evident the shrub community
is vigorous and expanding.
*
*
*
*
*
(c) * * *
(3) * * *
(i) Ten full years, except as provided
in paragraph (c)(3)(ii) in this section.
The vegetation parameters identified in
paragraph (b) of this section for grazing
land, pasture land, or cropland shall
equal or exceed the approved success
standard during the growing season of
any two years after year six of the
responsibility period. Areas approved
for the other uses identified in
paragraph (b) of this section shall equal
or exceed the applicable success
standard during the growing season of
the last year of the responsibility period.
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16:49 Aug 29, 2006
Jkt 208001
(ii) Five full years for lands eligible
for remining included in permits issued
before September 30, 2004, or any
renewals thereof. To the extent that the
success standards are established by
paragraph (b)(5) of this section, the
lands shall equal or exceed the
standards during the growing season of
the last year of the responsibility period.
*
*
*
*
*
PART 817—PERMANENT PROGRAM
PERFORMANCE STANDARDS—
UNDERGROUND MINING ACTIVITIES
4. The authority citation for part 817
continues to read as follows:
I
Authority: 30 U.S.C. 1201 et seq.
5. In § 817.22, revise paragraphs (d)(1)
introductory text and (d)(1)(i) to read as
follows:
I
§ 817.22
Topsoil and subsoil.
*
*
*
*
*
(d) * * *
(1) Topsoil materials and topsoil
substitutes and supplements removed
under paragraphs (a) and (b) of this
section shall be redistributed in a
manner that—
(i) Achieves an approximately
uniform, stable thickness when
consistent with the approved
postmining land use, contours, and
surface-water drainage systems. Soil
thickness may also be varied to the
extent such variations help meet the
specific revegetation goals identified in
the permit;
*
*
*
*
*
I 6. Amend § 817.116 as follows:
I A. Revise paragraph (a)(1);
I B. Revise the first sentence of
paragraph (b)(3) introductory text;
I C. Add five sentences to the end of
paragraph (b)(3)(ii);
I D. Revise paragraphs (c)(3)(i) and (ii).
The revisions read as follows:
§ 817.116
success.
Revegetation: Standards for
(a) * * *
(1) Standards for success and
statistically valid sampling techniques
for measuring success shall be selected
by the regulatory authority, described in
writing, and made available to the
public.
*
*
*
*
*
(b) * * *
*
*
*
*
*
(3) For areas to be developed for fish
and wildlife habitat, recreation,
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undeveloped land, or forest products,
success of vegetation shall be
determined on the basis of tree and
shrub stocking and vegetative ground
cover. * * *
(i) * * *
(ii) * * * The requirements of this
section apply to trees and shrubs that
have been seeded or transplanted and
can be met when records of woody
vegetation planted show that no woody
plants were planted during the last two
growing seasons of the responsibility
period and, if any replanting of woody
plants took place during the
responsibility period, the total number
planted during the last 60 percent of
that period is less than 20 percent of the
total number of woody plants required.
Any replanting must be by means of
transplants to allow for adequate
accounting of plant stocking. This final
accounting may include volunteer trees
and shrubs of approved species.
Volunteer trees and shrubs of approved
species shall be deemed equivalent to
planted specimens two years of age or
older and can be counted towards
success. Suckers on shrubby vegetation
can be counted as volunteer plants
when it is evident the shrub community
is vigorous and expanding.
*
*
*
*
*
(c) * * *
(3) * * *
(i) Ten full years, except as provided
in paragraph (c)(3)(ii) in this section.
The vegetation parameters identified in
paragraph (b) of this section for grazing
land, pasture land, or cropland shall
equal or exceed the approved success
standard during the growing season of
any two years after year six of the
responsibility period. Areas approved
for the other uses identified in
paragraph (b) of this section shall equal
or exceed the applicable success
standard during the growing season of
the last year of the responsibility period.
(ii) Five full years for lands eligible
for remining included in permits issued
before September 30, 2004, or any
renewals thereof. To the extent that the
success standards are established by
paragraph (b)(5) of this section, the
lands shall equal or exceed the
standards during the growing season of
the last year of the responsibility period.
*
*
*
*
*
[FR Doc. 06–7249 Filed 8–29–06; 8:45 am]
BILLING CODE 4310–05–P
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[Federal Register Volume 71, Number 168 (Wednesday, August 30, 2006)]
[Rules and Regulations]
[Pages 51684-51706]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-7249]
[[Page 51683]]
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Part III
Department of the Interior
-----------------------------------------------------------------------
Office of Surface Mining and Enforcement
-----------------------------------------------------------------------
30 CFR Parts 816 and 817
Topsoil Redistribution and Revegetation Success Standards; Final Rule
Federal Register / Vol. 71, No. 168 / Wednesday, August 30, 2006 /
Rules and Regulations
[[Page 51684]]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Office of Surface Mining Reclamation and Enforcement
RIN 1029-AC02
30 CFR Parts 816 and 817
Topsoil Redistribution and Revegetation Success Standards
AGENCY: Office of Surface Mining Reclamation and Enforcement, Interior.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: We, the Office of Surface Mining Reclamation and Enforcement
(OSM), are finalizing minor changes to our regulations to improve the
quality and diversity of revegetation in the reclamation of coal mined
lands. These revisions govern topsoil redistribution and revegetation
success standards and will: Encourage species diversity on reclaimed
lands by allowing replacement of soil in variable thicknesses; provide
more flexibility to States in using new vegetative success standards
and sampling techniques by removing the current requirement that such
changes be included in the approved regulatory program; define success
standards for lands with an undeveloped land postmining land use;
remove shelter belts from the list of postmining land uses subject to
success standards; provide more flexibility to operators when they
demonstrate compliance with time-in-place requirements by allowing them
to consider all trees and shrubs in place at bond release, including
volunteer trees and shrubs, and not requiring them to verify the length
of time that individual trees and shrubs have been in place--this
change will remove a significant impediment to reforestation of mined
lands; and make the timing of revegetation success measurements in
areas receiving 26 inches of annual precipitation or less consistent
with those in areas receiving more than 26 inches of annual
precipitation.
DATES: Effective Date: September 29, 2006.
FOR FURTHER INFORMATION CONTACT: Robert Postle, Office of Surface
Mining Reclamation and Enforcement, U.S. Department of the Interior,
P.O. Box 46667, Denver, CO 80201; Telephone: 303-844-1400, extension
1469. E-mail: bpostle@osmre.gov.
SUPPLEMENTARY INFORMATION:
I. Background Information on the Rulemaking
II. Discussion of the Revisions and Our Response to the Comments
Submitted
III. Procedural Matters and Required Determinations for This Rule
I. Background Information on the Rulemaking
Why are we revising our regulations?
On March 17, 2005, we published proposed revisions to our
regulations that govern portions of the performance standards dealing
with topsoil redistribution and evaluation of revegetation success. 70
FR 13076. The revisions contained in this final rule are the product of
several outreach efforts by OSM to review and assess its revegetation
regulations at Sec. Sec. 816.111 through .116 and Sec. Sec. 817.111
through .116. The first outreach effort occurred in 1999. As part of
this revegetation initiative, we published a Federal Register notice on
May 17, 1999 (64 FR 26773), announcing public meetings and soliciting
comments, concerns, and new ideas regarding the regulatory performance
standards that determine revegetation success. In the notice, we also
announced the availability of an OSM concept paper that reviewed
various longstanding revegetation issues. We held ten public meetings
around the country between May 27 and August 25, 1999. In the spring of
2003, as a follow-up to the 1999 revegetation initiative, we conducted
a survey of State regulatory authorities. This survey explored whether
the statistical and/or production requirements of the current
revegetation regulations at Sec. 816.116 and Sec. 817.116 adversely
affect the establishment of a diverse plant community; whether there is
a continuing need for inclusion of success standards and sampling
techniques in a State's approved program; and whether there is a need
for success standards for undeveloped postmining land.
In addition to the revegetation initiative and survey, we also
established a reforestation outreach initiative that began with three
workshops held between January 1999 and May 2002 involving Federal and
State regulatory personnel, industry representatives, and landowners.
As part of this second initiative, we raised the question whether
specific OSM regulations act as a disincentive to the choice of
forestry as a postmining land use.
Largely as a result of these revegetation and reforestation
initiatives and the survey, we identified five minor revisions that we
needed to make to the existing regulations. This rule revises the
Federal regulations governing the topsoil redistribution standards at
Sec. 816.22(d)(1) and Sec. 817.22(d)(1); the success standards and
sampling techniques requirements at Sec. 816.116(a)(1) and Sec.
816.117(a)(1); the land use categories subject to the success standards
at Sec. 816.116(b)(3) and Sec. 817.116(b)(3); the revegetation
success standards for trees and shrubs at Sec. 816.116(b)(3)(ii) and
Sec. 817.116(b)(3)(ii); and the timing of revegetation success
measurements at Sec. 816.116(c)(3)(i) and (ii) and Sec.
817.116(c)(3)(i) and (ii).
These revisions will, respectively, encourage species diversity on
reclaimed lands by allowing replacement of soil in variable
thicknesses; provide more flexibility to States in using new vegetative
success standards and sampling techniques by removing the current
requirement that such changes be included in the approved regulatory
program; define success standards for lands with an undeveloped land
postmining land use; remove shelter belts from the list of postmining
land uses subject to success standards; provide more flexibility to
operators when they demonstrate compliance with time-in-place
requirements by allowing them to consider all trees and shrubs in place
at bond release, including volunteer trees and shrubs, and not
requiring them to verify the length of time that individual trees and
shrubs have been in place--this change will remove a significant
impediment to reforestation of mined lands; and make the timing of
revegetation success measurements in areas receiving 26 inches of
annual precipitation or less consistent with those in areas receiving
more than 26 inches of annual precipitation. Since the soil
redistribution and revegetation success standards are identical for
surface and underground mining activities, this preamble will discuss
our revisions to part 816 with the understanding that the discussion
also applies to our revisions to part 817.
In response to the Federal Register notice of our 2005 proposed
rule, we received a total of 34 comments. We discuss the comments and
our responses to those comments below. No one requested a public
hearing.
II. Discussion of the Revisions and Our Response to the Comments
Submitted
1. Section 816.22(d)(1)(i): Topsoil Redistribution
What are the revisions to Sec. 816.22(d)(1)(i)?
In order to improve the potential for establishing diverse plant
communities consistent with the specific revegetation goals for an
approved postmining land use, we are adopting, as generally proposed
and further revised in response to comments received, topsoil
redistribution provisions at Sec. 816.22(d)(1)(i) that specify the
manner
[[Page 51685]]
in which topsoil material removed under Sec. 816.22(a) or (b) must be
redistributed. Final Sec. 816.22(d)(1)(i) will read as follows, with
new language in italics:
(d) Redistribution. (1) Topsoil materials and topsoil
substitutes and supplements removed under paragraphs (a) and (b) of
this section shall be redistributed in a manner that--
(i) Achieves an approximately uniform, stable thickness when
consistent with the approved postmining land use, contours, and
surface-water drainage systems. Soil thickness may also be varied to
the extent such variations help meet the specific revegetation goals
identified in the permit;
Under the prior topsoil redistribution regulations at Sec.
816.22(d)(1)(i), topsoil must be redistributed in a manner that
``achieves an approximately uniform, stable thickness consistent with
the approved postmining land use * * *.'' This requirement that topsoil
be redistributed (or ``replaced'') to an approximately uniform
thickness has proven to be particularly appropriate when the approved
postmining land uses are, for example, commercial forestry or cropland,
both of which may involve a single species of vegetative cover in a
managed agricultural environment. However, when the approved postmining
land uses are wildlife habitat or grazing land that require
satisfaction of specified vegetative diversity standards for bond
release, the requirement in Sec. 816.22(d)(1)(i) that topsoil be
replaced to an approximately uniform thickness may often work against
the achievement of those vegetative diversity standards. This is
because a plant community that will sustain itself without constant
management input is, to a considerable degree, a function of the
physical and chemical characteristics of the soil upon which it is
growing. In turn, variable topsoil depth is one of the several physical
characteristics that operators can use to encourage the desired species
diversity.
As discussed in the preamble to the proposed rule, when we first
promulgated our topsoil regulations over 20 years ago, we noted that
two commenters had objected to the proposed uniform thickness
requirement as being a design standard, not a performance standard. 48
FR 22092, May 16, 1983. These commenters warned that the rule's uniform
soil thickness requirement could lead to a monoculture vegetative
community rather than a diverse native species community. We did not
accept this comment, responding that topsoil thickness is but one of
several factors affecting plant growth and species diversification.
More recently, in response to our 1999 revegetation outreach
effort, commenters again questioned the appropriateness of the Sec.
816.22(d)(1)(i) provision, which they interpreted as requiring that
topsoil always be redistributed to a uniform thickness. These
commenters stated that uniform soil thickness tends to promote a
limited number of species in the vegetative cover while variable soil
thicknesses tend to promote a more diverse vegetative community. The
truth of this proposition has been born out by the experience of OSM
agronomists and is consistent with well-established principles of soil-
plant relationships. As proposed, we have revised our regulations at
Sec. 816.22(d)(1)(i) by adding a sentence that expressly allows soil
thickness to be varied to the extent such variations help to meet the
specific revegetation goals identified in the permit. Also as proposed,
we have inserted the word ``when'' between the words ``thickness'' and
``consistent'' in the existing language of Sec. 816.22(d)(1)(i). This
insertion should make clear that the uniform soil thickness provision
is a function of the approved postmining land use, contours, and
surface water drainage systems, and is not, in itself, an inflexible
requirement.
While the prior uniform topsoil redistribution standard of Sec.
816.22(d)(1)(i) has generally worked quite well, the new revisions to
that standard are intended to provide the operator with another tool
for encouraging the development of the diverse plant communities
required of specific postmining land uses. For example, if the
designated postmining land use is fish and wildlife habitat, and the
desired plant communities are a mixture of grasslands with interspersed
shrub and tree areas for wildlife cover, then the permit could describe
the use of variable topsoil thickness to ensure the establishment of
grasses on thicker soils and trees and shrubs on thinner soils. The
fact that the permit applicant must clearly set forth the justification
for any non-uniform redistribution of topsoil should largely protect
against potential abuse. This revised rule will not affect existing
topsoil salvage requirements.
In response to comments, we have further revised Sec. 816.22(d)(1)
to provide that topsoil materials and topsoil substitutes and
supplements removed under paragraphs (a) and (b) must be redistributed
in a manner that meets the requirements of subparagraphs (i)-(iii).
(Emphasis added). This last revision should make clear that, under
appropriate circumstances, the variable thickness revision of Sec.
816.116(d)(1)(i) applies to topsoil supplements and substitutes already
allowed under Sec. 816.22(a) and (b).
What were the comments submitted on our proposed revisions to Sec.
816.22(d)(1)(i)?
Seventeen commenters supported our proposed revision to the topsoil
redistribution requirements of Sec. 816.22(d)(1)(i). Their comments
focused on the potential to be gained from varying topsoil thickness in
establishing diverse plant communities. The commenters noted that
research supports our contention that topsoil thickness affects the
types, number, and densities of plants established in a particular
area. These commenters also generally supported our position that the
use of variable topsoil thickness to meet specific revegetation goals
identified in the permit will assist operators in establishing more
diverse plant communities on areas where such diversity is appropriate
to meet the postmining land use.
Four commenters proposed an additional revision to Sec.
816.22(d)(1). They suggested that we further amend Sec. 816.22(d)(1)
to apply to topsoil and topsoil supplements and substitutes removed
under paragraphs Sec. 816.22 (a) and (b) of this section. The
commenters indicated that the revision that we proposed inappropriately
applies only to topsoil materials as defined at Sec. 701.5, which
states that ``[t]opsoil means the A and E soil horizon layers of the
four master soil horizons.'' The commenters saw this as a problem
because western coal mines are often located in areas where the native
soils are poorly developed. At many of these mines, the A and E
horizons are absent or insufficient in thickness to provide sufficient
material for reclamation. Consequently, to meet their reclamation
goals, operators must rely on the use of suitable unconsolidated
materials immediately below the topsoil and on the use of selected
overburden as topsoil supplements and/or substitutes. The commenters
further noted that in other situations operators use very specific
topsoil substitutes to establish specific or unique plant communities.
For example, ongoing revegetation efforts have shown that substitute
materials with high rock fragment content are best for reestablishing
woody species in parts of the West. Accordingly, the commenters argued
that we needed to broaden our proposed revision to Sec. 816.22(d)(1)
to expressly allow for removed material, be it topsoil, topsoil
supplements, or topsoil substitutes, to
[[Page 51686]]
be replaced in variable thicknesses to meet specific revegetation
goals. According to commenters this change would allow western surface
coal mine operators to share in the benefits that our proposed rule was
intended to achieve.
We believe that these commenters have raised a valid concern about
the applicability of Sec. 816.22(d)(1) to the replacement of topsoil
supplements or to substitutes currently allowed under Sec. 816.22(b).
Many approved reclamation plans throughout the country already allow
the use of topsoil supplements or substitutes. Regulatory authorities
often permit use of such supplements or substitutes where there is
insufficient topsoil, defined as A and E horizon material, to ensure
the prescribed revegetation success. In other cases, they have approved
topsoil substitutes when applicants have demonstrated that the existing
topsoil is less suitable as plant growth material for the desired plant
community than available subsoil or spoil material. For many years we
have interpreted Sec. 816.22(d)(1) as applying to both topsoil
material removed under Sec. 816.22(a) and to topsoil supplements or
substitutes removed under Sec. 816.22(b). Pursuant to this
interpretation, once operators identify and remove approved topsoil
supplements or substitutes, they may treat this material as topsoil
material for the purposes of storage and redistribution. However, to
eliminate any potential confusion as to whether, under appropriate
circumstances, the variable thickness revision of Sec. 816.22(d)(1)(i)
applies to topsoil supplements and substitutes already allowed under
Sec. 816.22(a) and (b), we are accepting the comment and revising
Sec. 816.22(d)(1) as the commenters suggested. Accordingly, as set
forth above, final Sec. 816.22(d)(1) will provide that ``(1) Topsoil
materials and topsoil substitutes and supplements removed under
paragraphs (a) and (b) of this section shall be redistributed in a
manner that--'' (Emphasis added). Hereafter, references to variable
topsoil replacement also includes variable replacement of topsoil
substitutes and supplements.
Two commenters suggested eliminating from Sec. 816.22 (a) the
requirement to remove, i.e., salvage all topsoil. These commenters
contend that, based on our proposal to allow replacement of topsoil at
variable depths, we should be flexible and, at least in certain
circumstances, also allow operators not to remove and replace all
``available'' topsoil. They argued that to require removal of all
available topsoil would potentially defeat the purpose in the proposed
rule of allowing shallower topsoil depths. In addition, the commenters
pointed out that, according to mine reclamation professionals,
shallower topsoil depths increase plant community diversity and woody
stem density, while deeper than average topsoil depths (that would
compensate for the areas where topsoil is applied more shallowly than
the uniform average) only encourage aggressive grass and forb species
at the expense of diversity and woody stem density.
While the commenters are correct that shallower soils can increase
plant diversity and woody stem density, we are not revising the
regulations as they proposed. The existing regulations at Sec.
816.22(a) will continue to require the removal of all topsoil, defined
elsewhere as A and E horizon material. For several reasons we do not
believe that these regulations pose the problem suggested by the
commenters. Most importantly, section 515(b)(5) of the Surface Mining
Control and Reclamation Act of 1977 (SMCRA or the Act), clearly
requires the removal and replacement of all suitable topsoil.
Furthermore, natural landscapes usually include areas with deep soils
as well as shallower soils. This in turn results in multiple distinct
plant communities across the landscape. When we require uniform soil
thickness for reclamation, the result may be a single plant community
but little plant community variability across the landscape.
Conversely, when we require reclamation that includes areas with deep
soils as well as shallower soils, the result is more likely the
establishment of multiple diverse plant communities, including those
that prefer deeper soils as well as those that prefer shallower soils.
The purpose of the rule is not, as commenters characterize, to allow
for shallower topsoil depths throughout the reclamation area. Instead,
the rule requires removal of all topsoil to allow development of
reclamation and revegetation plans that can maximize the use of that
topsoil through the placement of variable topsoil depths and the
reconstruction of a much more diverse landscape similar to that which
may have existed prior to mining.
One commenter indicated that, if we allow variation in soil
thickness (specifically reductions in soil thickness), we must also
require the operator to demonstrate that an equal or greater chance for
sustaining vegetation success will result. In addition, the commenter
stated that the operator should have to demonstrate that the
reconstructed soil has a root zone of sufficient depth to support the
approved postmining land use.
We generally agree with this comment but do not believe that any
change in the revised regulation is necessary to ensure the desired
variation of soil thickness. The revised language of Sec.
816.22(d)(1)(i) allows operators to vary soil thickness to the extent
necessary to meet the specific revegetation goals identified in the
permit. In turn, these revegetation goals should support the approved
postmining land use. The State and the public will have the opportunity
to review the permit prior to approval and determine whether the
permittee has justified the need for variable topsoil thicknesses in
order to achieve the identified revegetation goals. If the permittee
has failed to do so, the State can disapprove the use of variable
topsoil thicknesses or require additional information to justify
departure from the normal practice. On this basis, we do not believe
that the demonstration proposed by the commenter is necessary.
One commenter opposed our proposed revision to the topsoil
redistribution requirements of Sec. 816.22(d)(1)(i). Instead of
replacing all the soil that was lost to strip-mining, the commenter
alleged that, under revised Sec. 816.116(d)(1)(i), coal companies
could replace only some of the removed soil. The commenter opposed the
change to Sec. 816.22(d)(1)(i) because, according to him, it could
``let coal companies do even less to bring the land they've mined back
to its original condition.''
This commenter seems to have misunderstood our proposal. It does
not scrap the current standard. As before, the revised regulation will
require operators to remove all topsoil from areas that are to be
disturbed by mining. After mining, they must redistribute all removed
topsoil on areas disturbed by mining. The proposed and final rules
merely allow operators whose reclamation plan and postmining land use
require the establishment of diverse plant communities as part of
specific revegetation goals identified in the permit to redistribute
topsoil at variable thicknesses rather than at approximate uniform
thickness. For the reasons stated above, we believe that the revision
to Sec. 816.22(d)(1)(i) will result in improved and more diverse
reclamation.
Another commenter observed that the proposed revision to Sec.
816.22(d)(1)(i) will require better planning on the part of companies
at the permitting stage, and that they must complete all vegetation
planning prior to completion of rough grading and prior to topsoil
replacement. The commenter, however, expressed concern that those who
[[Page 51687]]
thought that the proposal would make reforestation more successful may
be disappointed.
We strongly agree that allowing variable topsoil thickness under
the new provisions of Sec. 816.22(d)(1)(i) will require appropriate
planning by operators. As expressly stated in final Sec.
816.22(d)(1)(i), operators can vary soil thickness only if they justify
this variation based on specific revegetation goals identified in the
permit. The permit would necessarily have to include a discussion of
plans for variable topsoil thickness. Furthermore, an approved permit
would have to be in place prior to implementation of any plan for
regrading, topsoil redistribution, or revegetation. While there can be
no guarantee as to how much the revision to Sec. 816.22(d)(1)(i) will
actually increase reforestation of reclaimed areas, we reasonably
believe that the revision should encourage reforestation and species
diversity.
Another commenter suggested that we should broaden the proposed
revision to Sec. 816.22(d)(1)(i) to allow variable replacement
thicknesses for (1) suitable unconsolidated materials located
immediately below the topsoil, and (2) selected overburden used as
topsoil supplements and/or substitutes when the use of such materials
would help to meet the reclamation goals identified in the permit. In
the course of its own reclamation activities this commenter had found
that selected overburden materials, including scoria of suitable
fragment size range, are vitally important to creating diverse
vegetation types such as open scrub, and highly conducive to
establishing several shrub species in the genus Artemisia.
With regard to the commenter's first suggestion, we note that Sec.
816.102(f) already addresses the thickness of the suitable
unconsolidated material that is replaced below the topsoil. The
regulation expressly requires that exposed coal seams, acid- and toxic-
forming materials, and combustible materials exposed, used, or produced
during mining must either be adequately covered with nontoxic and
noncombustible material, or treated, to control the impact of the
materials on surface and ground water in accordance with Sec. 816.41,
to prevent sustained combustion, and to minimize adverse effects on
plant growth and the approved postmining land use. Section 816.102(f)
does not specify the thickness of the layer of nontoxic material that
must cover acid- and toxic-forming materials. The regulation thus
permits variable redistribution thicknesses of suitable unconsolidated
material that is found below the topsoil. As to the commenter's second
proposal, we have already stated that Sec. 816.22(d)(1)(i) properly
applies to topsoil supplements and substitutes and have revised the
regulation to clarify this point. Accordingly, final Sec. 816.22(d)(1)
will apply to both topsoil removed under Sec. 816.22(a) and topsoil
supplements and substitutes used in accordance with Sec. 816.22(b).
Another commenter indicated that the proposed revision to Sec.
816.22(d)(1)(i) allowing for variable soil thickness was unnecessary
for achievement of our stated purpose of encouraging greater plant
diversity. This commenter asserted that the existing rules afford
operators the flexibility to vary soil thicknesses in appropriate
cases. The commenter stated that reclamation plans within a single
permit area can be, and have been designed to accommodate the needs of
croplands, grasslands, and woodland plants by varying soil thicknesses
in the areas where each vegetation type will be planted. According to
the commenter, several other factors have far more influence upon the
diversity of the post-mining vegetative communities than do variable
soil thicknesses. These factors include the particular vegetation that
is to be planted after mining, the quality of the soil replaced, and
the degree to which soil compaction is prevented. The commenter
continued that the current regulation at Sec. 816.22(d)(1)(i)
requiring the replacement of an approximately uniform thickness of
topsoil provides for the protection, use, and productivity of soil
resources in a way that should restore the capability of the land to
support a wide variety of vegetation types and land uses. In support of
our retaining the longstanding provisions of Sec. 816.22(d)(1), the
commenter emphasized that the segregation and replacement of topsoil
over entire reclaimed areas has been successful over the fifty-seven
years of regulating the restoration of mined lands. This commenter
further noted that the proposed revision to Sec. 816.22(d)(1)(i) would
not provide minimum thickness requirements for topsoil redistribution.
The commenter cautioned that, while variable topsoil thickness may
improve attainment of certain land use types, too thin a layer of
topsoil could prove counterproductive to the attainment of ground
cover, erosion protection, water quality protection, and restoration of
productive capability of the land. The commenter concluded, therefore,
that any provision allowing replacement of variable topsoil or topsoil-
substitute thicknesses should also provide for a minimum topsoil or
soil-substitute thickness. This commenter also indicated that his
experience is not consistent with the statement in our preamble that
``[t]he fact that a permit applicant must clearly set forth the
justification for any non-uniform redistribution of topsoil should
largely protect against potential abuse.'' According to the commenter,
it would be easier for a regulatory authority to sustain challenges to
a finding of non-compliance with a specific performance standard, e.g.,
that operators must redistribute topsoil in an uniform thickness, than
to sustain challenges to a finding that the operator has not adequately
set forth the justification for non-uniform thicknesses.
We disagree with these comments and concerns. Most importantly, we
do not consider that the revision to Sec. 816.116(d)(1)(i) represents
a reduction of the regulatory standards. As discussed in the preamble
to our proposed rule and as reflected in the express language of that
rule, we intend to allow variable topsoil thicknesses when necessary to
further the specific revegetation goals identified in the permit. The
fact that the permit application must clearly set forth the
justification for variable topsoil thicknesses reasonably protects
against potential abuse. If the regulatory authority finds that
redistribution of topsoil in variable thicknesses is not necessary to
meet the specific revegetation goals identified in the permit
application, then the authority need not approve that aspect of the
application. If, however, the regulatory authority finds that variable
topsoil thicknesses is desirable, the permit application should specify
the amount of variability allowable and the minimum acceptable topsoil
thickness. Contrary to the commenter's experience, research in the West
on the impact of topsoil depth on plant diversity has shown that plant
diversity can be improved with redistribution of variable topsoil
thicknesses. Long-Term Plant Community Development In Response to
Topsoil Replacement Depth On Mined Land In Wyoming, C.K. Bowen, G.
Schuman, and R.A. Olson, American Society of Mining and Reclamation,
2005. Long-Term Effects of Cover Soil Depth On Plant Community
Development for Reclaimed Mined Lands in New Mexico, B. Buchanan, M.
Owens, J. Mexal, T. Ramsey, and B. Musslewhite, American Society of
Mining and Reclamation, 2005.
The same commenter also expressed concern both about the effect
that proposed Sec. 816.22(d)(1)(i) would have on the restoration of
premine land
[[Page 51688]]
capability and the negative effect that the revised regulation would
have on one of the basic missions of SMCRA-assuring that required
reclamation accounts for the capability of the land prior to any mining
to support a variety of uses. Simply stated, the commenter urged us not
to stress vegetation diversity at the expense of the underlying land
capabilities. The commenter also indicated that, in those areas of the
country where valuable topsoil resources exist, regulatory authorities
must take into account soil rooting zone reconstruction for the proper
utilization of those soil resources. This reconstruction should be done
in a way that would provide not only for tree productivity but also for
use of the soil resources in a manner that would maximize the post-
mining capability of the land. Furthermore, the commenter stated that
it is not necessary to relocate, modify distribution, or eliminate
topsoil resources in order to ``encourage'' reforestation as a
postmining land use. The commenter concluded by characterizing our
stated basis for revising Sec. 816.22(d)(1)(i) as ignoring ``the
essential nature and role of topsoil resources in land use capability
and suitability to support a variety of uses.''
We agree with the commenter that topsoil resources must be
protected. The regulations at Sec. 816.22(a) and (d) continue to
require that all topsoil must be removed and that all removed topsoil
must be redistributed. The revised regulation at Sec. 816.22(d)(1)(i)
simply provides the opportunity to allow redistribution of topsoil at
variable thickness when such redistribution is appropriate to meet the
revegetation goals identified in the permit's approved postmining land
use plan. Under the existing regulations in Sec. 816.22(e), a
regulatory authority can also require removal and redistribution of
subsoil, if necessary, to comply with the revegetation requirement of
the regulations. The proposed and final rules do not, therefore, ignore
or negate the existing land use provisions of Sec. 816.133(a), which
require that all disturbed areas be restored in a timely manner to
conditions that are capable of supporting the uses they were capable of
supporting before mining, or higher or better uses. Under these rules,
if the regulatory authority determines that the proposed redistribution
of topsoil in varying thicknesses would adversely affect the
restoration of the land use capability of an area, then the regulatory
authority need not sanction such redistribution.
Another commenter noted that the revised regulation, which allows
soil thickness to be varied to the extent that such variation
encourages the specific revegetation goals identified in the permit,
needs to include a modification and verification provision that would
assure that variation is not a post hoc effort by the operator to avoid
proper redistribution of topsoil. The commenter also stated that the
rule must clarify that operators may not vary topsoil and subsoil
redistribution in those instances where removal and reconstruction of
soils is necessary to restore mined farmland. The commenter next argued
that the rule's standard for justifying variation in topsoil
replacement thickness should be more precise and measurable than merely
providing that the variation ``help meet'' the specific revegetation
goals identified in the permit. In this regard, the commenter stated
that the permit should define the amount of variability in topsoil
thickness and the chemical quality of the topsoil necessary to meet
identified revegetation goals. Where uniform thickness is not to be the
standard, the topsoil and subsoil redistribution plan should also
provide appropriate literature citations supporting the proposition
that the variation of soil thicknesses is consistent with, and
necessary for, the success of particular species. Finally, this
commenter asserted that, regardless of whether the soil thickness is
intended to be relatively uniform or varied to support a particular
species or mixture of vegetative cover on the reclaimed land, the State
regulatory authority or OSM, acting under a Federal Program, should
require the operator to demonstrate compliance with the soil
redistribution requirements of Sec. 816.22(d)(1)(i). Furthermore, the
State regulatory authority or OSM should take sufficient soil thickness
measurements to support a finding of compliance.
We believe that the current and revised regulations at Sec.
816.22(d)(1)(i) adequately address the concerns underlying these
comments. The new provisions of Sec. 816.22(d)(1)(i) that soil
thickness may be varied to the extent that such variations help meet
the specific revegetation goals identified in the permit clearly
implies the need for the operator to document how topsoil will be
redistributed prior to such redistribution. This necessary
documentation should ensure that the redistribution of topsoil at
varied thicknesses is not a post hoc effort to avoid proper
redistribution. For example, if the approved postmining land use is
cropland, then redistribution of topsoil at varied thicknesses would
not be appropriate and operators should redistribute the topsoil in an
approximately uniform thickness as is presently required. However, if
the approved revegetation goals would best be met by varying topsoil
thicknesses, then the operator must propose and the regulatory
authority must approve these variations. While we believe that
authoritative literature and/or test plots are appropriate sources of
information for setting sideboards on the variation in topsoil
thickness, we leave to the discretion of the regulatory authority
whether to require inclusion of such literature or test plot data in
the permit. Evaluation of the thickness of redistributed topsoil based
on permit specifications can be done either as part of the ongoing
inspection process or based on data submitted by the operator. In this
regard, we anticipate that the regulatory authority will evaluate the
redistribution of topsoil in varying thickness in the same manner that
it currently evaluates the redistribution of topsoil in an
approximately uniform thickness under prior Sec. 816.22(d)(1)(i).
2. Section 816.116(a)(1): Federal Approval of Revegetation Success
Standards
What are the revisions to Sec. 816.116(a)(1)?
We have revised Sec. 816.116(a)(1) to eliminate the requirement
that revegetation success standards and statistically valid sampling
techniques be included in the approved regulatory program (hereinafter
``the approved program requirement''). The revised regulation continues
to require that standards for success and sampling techniques for
measuring success must be selected by the regulatory authority. Our
proposed elimination of the approved program requirement was described
in our 2005 Federal Register notice. As a result of comments received
and discussed below, we are also adding a provision to Sec.
816.116(a)(1) to clarify that the standards and techniques selected by
the regulatory authority shall be described in writing and made
available to the public. Later in this document we describe several
acceptable means for making the standards and techniques available to
the public. Final Sec. 816.116(a)(1) will read as follows, with new
language in italics:
(1) Standards for success and statistically valid sampling
techniques for measuring success shall be selected by the regulatory
authority, described in writing, and made available to the public.
[[Page 51689]]
Why are we changing our policy regarding review of State Program
changes in success standards and sampling techniques?
As explained in more detail below, the requirement that State
regulatory authorities include the initial or amended success standards
and sampling techniques for revegetation as part of their approved
program imposes a significant and unnecessary burden both on State
regulatory authorities and OSM. Our regulations at Sec. 816.116(a)(2)
and (b), which will remain in effect, already specify minimum criteria
for success standards and sampling techniques, and those criteria will
ensure the achievement of SMCRA's goal of establishing a diverse,
permanent, and effective vegetative cover. Section 816.116(a)(2)
provides that the sampling techniques must use a 90-percent confidence
interval (also known as a one-sided test with a 0.10 alpha error),
which was discussed in the preamble to the proposed rule, and that the
ground cover, production, or stocking must meet 90-percent of the
success standard. Section 816.116(b) provides additional guidelines for
particular types of ecosystems and post-mining land uses. These key
nationwide minimum protections will remain in the regulations as
amended, and all approved State programs must maintain counterparts to
them.
In our judgment, it is not a good use of State and Federal
resources to continue requiring State and OSM revegetation experts to
spend valuable time on preparing or assessing new State program
amendment proposals every time it is necessary to revise or improve
revegetation success standards. A number of considerations support this
conclusion. First, the amount of time and resources required to go
through the State program amendment process is significant and we think
discourages updating the success standards and sampling techniques. Our
processing of program amendments takes an average of about four and a
half months, ranging from two and a half to seven months, but one
recent amendment took twenty months from proposal to final approval.
The time and resources spent on the program amendment process,
moreover, are in addition to those the States must devote to preparing
proposed program amendments and to responding to any of our inquiries.
Although we lack complete data on how great a burden this regulatory
requirement imposes on the States, the example of North Dakota, which
follows, shows that the cumulative costs in time and talent can be
quite large. The present component of the North Dakota State program
for revegetation success standards and sampling techniques is now more
than 100 pages long. North Dakota has repeatedly had to submit proposed
amendments for our approval not only for substantive changes in
standards but even for minor wording changes, such as the change in the
name of a U.S. Department of Agriculture bureau from the ``Soil
Conservation Service'' to the ``Natural Resources Conservation
Service.'' On this basis alone, we think that the current requirement
may well be discouraging State regulatory authorities from developing
or implementing the latest, most appropriate science and technologies.
70 FR 13076, March 17, 2005. This apparent obstacle to the timely
development of new science and technologies also runs counter to one of
the main concerns behind our 1983 rulemaking: That the States needed
significant flexibility to tailor standards and sampling techniques to
local conditions. See 47 FR 40140, September 2. We continue to want to
encourage responsible innovation in this area. As we mentioned in the
preamble to our 2005 proposed rule, we have been working with western
States to develop new success standard resources, innovative
statistical tools, and techniques using computers and satellite-based
remote sensing technologies to better evaluate conditions of vegetative
diversity and cover than is possible using traditional sampling
methods, particularly in locations with naturally sparse vegetation. In
the Appalachian Region, our agency is working with scholars and the
State of West Virginia on the use of the plate method for evaluating
herbaceous productivity on reclaimed lands. We believe that removal of
the requirement in Sec. 816.116(a)(1) for including these standards
and techniques in the approved program will eliminate an unnecessary
obstacle to appropriate and timely technological innovation.
Second, we recognize that, since the basic framework of the
existing rule was first promulgated in 1983, the vast majority of State
regulatory programs have matured. Our experience with the State
regulatory authorities over the years has shown that they now have
sufficient expertise to devise or modify their success standards and
sampling techniques to incorporate new scientific, technological, or
other information in a manner that assures proper revegetation of
disturbed areas. In most instances, we have not had to engage in
substantial re-writing of changes to State revegetation success
standards or sampling techniques during the Federal approval process.
However, even though we will no longer be approving State program
amendments on those issues, our revegetation experts will remain
available to consult with the State regulatory authorities on issues
including success standards and sampling techniques. Thus, our agency
is not withdrawing resources that have been beneficial to the States as
they pursue SMCRA's goal of successful revegetation.
Third, and perhaps most importantly, the removal of the approved
program requirement from Sec. 816.116(a)(1) leaves no regulatory void.
As previously noted, the nationwide minimum requirements for
revegetation success and sampling techniques will continue to apply to
the State regulatory authorities and indirectly to the permits that
those regulatory authorities issue. Thus, the revision to Sec.
816.116(a)(1) will not cause greater divergence among the States that
are already required to meet the minimum nationwide requirements of
Sec. 816.116(a)(2) and (b). Even in those States that by State law are
not allowed to be more stringent than OSM's regulations, the minimum
nationwide requirements of Sec. 816.116(a)(2) and (b) continue to
apply. While complying with those nationwide requirements, the State
regulatory authorities will, under revised Sec. 816.116(a)(1), also be
able to respond to new or localized scientific, technical, and land use
information in a timelier manner, without awaiting the formal process
of OSM approval. Furthermore, there are avenues besides our approval of
success standards and sampling techniques by which the public and we
may assure compliance by the State regulatory authorities with
nationwide revegetation requirements. The success standards and
sampling techniques will have to be included in each permit issued by
the State regulatory authorities. Thus, contrary to the assertions of
one commenter, the removal of this requirement will not lead to
compromises in the effective implementation of SMCRA's goal of proper
revegetation. In addition, ``any person with an interest which is or
may be adversely affected may request a hearing'' on any permit issued
by a State regulatory authority. Sec. 775.11(a). When a permittee
applies for final bond release, the surface owner must be notified and
given an opportunity to participate in the bond-release inspection.
Sec. 800.40(b)(1). Before final bond release, any person with a valid
legal interest may file objections and
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request a public hearing. Sec. 800.40(f). The State's regulatory
program must also provide for administrative hearings and judicial
review. Sec. Sec. 775.12(b) and 775.13(b). In addition, if, in
conducting an oversight inspection, we were to find a surface coal
mining operation in violation of the nationwide minimum requirements,
we would take appropriate action. See Sec. 842.11(a)(1),
(b)(1)(iii)(A). If the State appears to be including success standards
and sampling techniques in its permits that are not in compliance with
the nationwide minimum requirements of Sec. 816.116(a)(2) and (b), we
can initiate proceedings that could ultimately lead to substitution of
direct Federal enforcement of the revegetation requirements, or
withdrawal of the Secretary's approval of the State program in whole or
in part. Sec. 733.12(a), (g). Thus, the public's interest in proper
revegetation remains protected, and the State regulatory authorities
have incentive to keep their success standards and sampling techniques
in compliance with the nationwide minimum requirements that have
applied since 1983.
A final reason for removing the requirement that revegetation
success standards and sampling techniques be included in the approved
program is that this requirement is inconsistent with the approach we
have taken in other areas. States do not have to include in their
approved programs all of the specific techniques and standards they use
to assess whether other SMCRA requirements have been met. See Sec.
780.22 (requiring submission of the geologic data and overburden
characteristics), Sec. 780.21(d) (requiring assessment of the probable
hydrologic consequences of mining), and Sec. 780.21(g) (requiring a
cumulative hydrologic impact assessment showing, inter alia, that the
operation has been designed to prevent material damage to the
hydrologic balance outside the permit area but not defining the term
``material damage''). Instead, the regulatory authorities, both States
and OSM, have effectively addressed the standards to be used in these
determinations or submissions by developing guidance documents that are
not required to be in the approved regulatory programs. Moreover, we do
not impose the requirement to promulgate success standards and sampling
techniques upon ourselves when we act as a regulatory authority. None
of the three Federal programs with active mining include specific
vegetation sampling techniques. The Federal program for the State of
Washington and the Federal program for Indian lands do not include
specific revegetation success standards; the only Federal program with
active mining that includes such requirements is the regulatory program
for Tennessee. Sec. Sec. 942.816(f) and 942.817(e). We have no
compelling justification for continuing such an inconsistent approach,
particularly since there is no reason to believe that the different
requirements of State and Federal programs have resulted in significant
divergence of the actual success standards or sampling techniques in
use, or in the actual success of revegetation on mined sites. There is
thus no principled reason to believe that the States cannot effectively
implement revegetation success standards and sampling techniques
without having to go through the formal promulgation process imposed by
the prior approved program requirement of Sec. 816.116(a)(1).
What were the comments submitted on our proposed revisions to Sec.
816.116(a)(1)?
In response to our proposed rule, we received comments from 16
commenters supporting removal of the approved program requirement from
Sec. 816.116(a)(1). Of the 16 commenters, five were State regulatory
authorities, one was a State coal association, six were coal companies,
and four were industry associations. In general, these commenters based
their support on the reduced regulatory burden they affirmed would
result from eliminating the (a)(1) requirement. They also stated that
the proposal would result in increased flexibility and improve their
ability to make use of potential new technologies that may become
available. Specific comments stated that the current process provides
little incentive to continue or expand research into new and innovative
methods, often results in unnecessary delays in State implementation of
changes to these policies that are based on a State's professional
judgment, and flies in the face of State primacy. These commenters
stated that the revised regulation will better enable States to stay
abreast of technological advances and to tailor success standards to
local conditions, will allow use of alternative parameters for
revegetation success, such as measurement of a site index, without
submitting program amendments. Furthermore, the revised regulations
will still support strict revegetation standards while allowing States
to respond to improvements in sampling methodologies and technological
advances.
We agree with these commenters and are proceeding with the
rulemaking as proposed. The revised regulation will give the States the
flexibility they need to implement new technologies without having to
go through the Federal rulemaking process of amending their approved
programs. As discussed above, we are also adding a provision to Sec.
816.116(a)(1) to clarify that the standards and techniques selected by
the regulatory authority must be described in writing and made
available to the public. This last provision will ensure that all
interested parties can readily find out all the options available in
their jurisdiction for evaluating revegetation success.
Four of the commenters that supported the proposed revision to
Sec. 816.116(a)(1) noted that the revision, and the regulation as a
whole, does not reflect that standards of success and statistically
valid sampling techniques for measuring success are actually developed
jointly by the permit applicant and regulatory authority and
incorporated as part of the reclamation plan approved as part of the
permit. These commenters indicated that normally the operator proposes
such standards and sampling techniques prior to conducting baseline
vegetation studies. The commenters agreed that this is appropriate, as
the operator is most familiar both with the plant communities that will
be affected by the operation and with the sampling methods needed to
accurately describe and measure these plant communities. The commenters
indicated that the standards and sampling techniques will become
subject to evaluation in the permitting process and will be ultimately
codified in the permit or letters of concurrence from regulatory
authorities. The commenters further noted that through this process
sampling methods and success standards are not ``selected''
unilaterally by the regulatory authority. Accordingly, the commenters
suggested that preamble language of the Sec. 816.116(a)(1) revision be
improved by emphasizing the current process by which a number of the
State regulatory authorities and their permittees jointly develop
success standards and sampling techniques.
We are retaining the current requirement of Sec. 816.116(a)(1)
that the regulatory authority select revegetation success standards and
statistically valid sampling techniques. The selected success standards
and sampling techniques will be put in writing and be available to the
public and, as before, will be used by operators in developing their
permit applications. The manner
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in which a regulatory authority goes about selecting the success
standards and statistically valid sampling techniques that it will
allow operators to use in evaluating revegetation success is up to the
regulatory authority. That authority can, as suggested by the
commenters, select the success standards and sampling techniques in
consultation with operators and/or with assistance from academia.
However, selected success standards and sampling techniques must meet
the requirements of Sec. 816.116(a)(2) and (b) and they must be put in
writing and made available to the public. It is from these identified
success standards and sampling techniques that the operators must
choose the specific standards and techniques included in their
individual permit applications. This procedure will ensure no less
consistent revegetation success evaluations than that afforded under
the prior rule.
We received comments from five commenters opposed to the proposed
revision deleting the approved program requirement from Sec.
816.116(a)(1). A large percentage of these comments focused on the
absence of any provision in the proposed rule that would provide for
public review of the success standards and sampling techniques selected
by the regulatory authority. More specifically, these comments raised
concerns about loss of public review; lack of enforceable success
standards; inability of the public to review permits if the success
standards and sampling techniques are not part of the approved program;
and potential conflict among States, operators, and landowners over
acceptable standards and sampling techniques. Other commenter concerns
focused on the lack of support for changing a regulation that had been
in place since 1983 and the inability of Federal oversight to prevent
problems. These commenters also stated that the burden of OSM's lengthy
timeframes for processing State amendments is self-imposed, that
flexibility already exists within the Federal regulations for States to
develop success standards and sampling techniques to fit local
conditions, that inconsistent application of success standards and
sampling techniques will occur, and that the current process does not
stifle evaluation or utilization of new technologies. The specific
comments received and our responses are discussed below.
All five of the commenters opposing removal of the approved program
requirement from Sec. 816.116(a)(1) expressed concern with the loss of
public review of selected success standards and statistically valid
sampling techniques if the standards and techniques were no longer
included in the State approved program. These commenters declared that
the removal of success standards and sampling techniques from the State
approved programs would result in information not being available to
the public. One of the commenters asserted that OSM, by adopting this
change, was taking the attitude that the only parties at interest in
these matters were the companies and the States. This commenter claimed
that success standards for reclamation are an extremely important
source of public information and that, under the proposed rule, it
would be more difficult for the public to find the success standards
approved for a given permit. The commenter indicated that the inclusion
of important matters in ``internal guidance documents'' and ``technical
standards'' alone is not satisfactory. The commenter further questioned
how, under the proposed rule, the public would know if there was any
internal consistency within and between States as to selected success
standards or sampling techniques. Finally, the commenter asserted that
under the proposed rule, as under the provisions for public review
during permitting at Sec. 773.6(a) and (b)(2), and as under the
provisions for public involvement in bond release at Sec. 800.40(b)(1)
and (f), OSM and the States seemingly want the public to find the
problems that OSM and the States have missed. The commenter concluded
that it would be hard for the public to find these problems if the
success standards and sampling techniques are not in the State
regulations.
Two of these commenters further noted that removal of the approved
program requirement from Sec. 816.116(a)(1) eliminates the ability of
the public to comment on the success standards and sampling techniques
proposed by the States for inclusion in their approved programs.
In partial response to these commenters' concerns, we are adding
the express requirement in final Sec. 816.116(a)(1) that the standards
and techniques selected by the States be in writing and made available
to the public. We did not include this requirement in the 2005 proposed
rule. Under the prior version of Sec. 816.116(a)(1), States were
required to include selected standards and techniques in their approved
programs but were not required to include them in the rules of their
approved programs. Rather, States had the option of including them in
any element of their approved programs including guidelines, technical
procedures, policy materials, etc. States will continue to have the
option of including selected success standards and sampling techniques
in the same range of formats, but must ensure their public
availability. For example, States could make this information available
to the public at places where other documents such as permit
applications are also made available for public review. Or the States
could further make it available to all interested parties either by
mail or through the agency's web site. As before, States will continue
to have the option of including selected standards and techniques in
their approved program regulations. Whatever the formats chosen by the
States, final Sec. 816.116(a)(1) ensures the public access to and,
therefore, the ability to review the selected standards and techniques.
Furthermore, there will continue to be ample opportunity on a permit-
specific basis for public review of the proposed use of selected
standards and sampling techniques both during the permitting process as
well as at bond release. Because Sec. 780.18(b)(5) requires each
permit application to identify its proposed success standards and
sampling techniques, this information is also available for public
review. Parties who have an interest that may be adversely affected by
a decision on the application may further comment on these standards
and sampling techniques under Sec. 773.6(a) and (b)(2). These
provisions ensure that the public will continue to have the ability to
review the success standards and sampling techniques for every mine
before operations begin. In addition, any persons with valid legal
interests can also object to bond release under Sec. 800.40(f) should
they believe the operator has not used the approved success standard or
not followed the approved sampling techniques.
Three of the five commenters opposing removal of the approved
program requirement from Sec. 816.116(a)(1) warned against the
disputes that they asserted would inevitably arise between States and
permit applicants/operators and between operators and landowners over
what constitutes appropriate success standards and/or sampling
techniques. The first of these three commenters admitted that the
proposed revision would provide flexibility to State programs and would
allow both States and operators to take advantage of new technology,
sample methods, and statistics. This commenter also conceded that the
approved program requirement of Sec. 816.116(a)(1) was unnecessarily
burdensome in terms of
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the time and resources required by the State program amendment process
and that this burden discourages updating revegetation standards.
Nonetheless, this commenter asserted that any flexibility gained by the
proposed revision to 816.116(a)(1) would not offset the endless
disputes that would inevitably arise between States and permit
applicants over what constitute acceptable methods and statistics.
While we believe that this commenter overstates the potential for
disputes between States and permit applicants under proposed Sec.
816.116(a)(1), final Sec. 816.116(a)(1) expressly requires that all
State-selected standards and techniques be in writing and made
available to the public. This new provision should minimize disputes
between a State and applicants over the range of success standards and
sampling techniques available within that State. As under the prior
rule, the permit applicant will be able to choose only from among
available success standards and sampling techniques previously selected
by the State. As under the prior rule, moreover, an applicant's
proposed use of a selected standard or technique will be subject to
State approval. Importantly, the potential for disputes between the
regulatory authority and permit applicant should not be any greater
than under the prior rule.
Two of the five commenters expressed additional concerns over the
potential conflict that might arise between landowners and operators as
a result of the proposed revision to Sec. 816.116(a)(1). One of these
two commenters also declared that the deletion of the approved program
requirement would potentially place the landowner and operator in
conflict at the time of bond release due to the use of measurement
standards that lack a robust scientific basis.
We do not believe that the deletion of the approved program
requirement from Sec. 816.116(a)(1) will materially raise the
potential for conflict between the landowner and operator at the time
of bond release. As stated earlier, the provisions of Sec.
816.116(a)(2) and (b) will continue to establish clear criteria and
requirements for the success standards and sampling techniques that may
be selected by the States under Sec. 816.116(a)(1). All approved
programs have counterparts to Sec. 816.116(a)(2) and (b). Accordingly,
the success standards and statistically valid sampling techniques
selected by a State under final Sec. 816.116(a)(1) will, for the
purposes of establishing revegetation success at bond release, have the
same robust scientific basis as the standards and techniques selected
by the State under the prior rule.
One of the commenters opposing removal of the approved program
requirement from Sec. 816.116(a)(1) suggested that, without including
success standards and measuring techniques in the approved State
program, operators may simply choose not to comply with selected
standards and techniques.
With regard to this concern, we note that all State approved
programs have counterparts to Sec. 780.18(b)(5) requiring that
applications for a permit contain a plan for revegetation, including
measures to determine the success of revegetation. Once approved by the
regulatory authority, these and all other permit terms are binding and
enforceable.
Still another commenter asserted that the reasons given by us for
this removal do not support abrupt departure from more than two decades
of regu