Endangered and Threatened Wildlife and Plants; Proposed Designation of Critical Habitat for the Zuni Bluehead Sucker, 5351-5369 [2013-01302]
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Federal Register / Vol. 78, No. 17 / Friday, January 25, 2013 / Proposed Rules
• Mail: Send written comments to
Juiyu Hsieh, RCRA Waste Management
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Remediation and Restoration (OSRR07–
1), EPA New England—Region 1, 5 Post
Office Square, Suite 100, Boston, MA
02109–3912
• Hand Delivery or Courier: Deliver
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email at hsieh.juiyu@epa.gov.
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SUPPLEMENTARY INFORMATION:
Dated: January 4, 2013.
Ira W. Leighton,
Acting Regional Administrator, EPA New
England, Region 1.
[FR Doc. 2013–01440 Filed 1–24–13; 8:45 am]
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–R2–ES–2013–0002;
4500030114]
RIN 1018–AZ23
Endangered and Threatened Wildlife
and Plants; Proposed Designation of
Critical Habitat for the Zuni Bluehead
Sucker
Fish and Wildlife Service,
Interior.
ACTION: Proposed rule.
AGENCY:
We, the U.S. Fish and
Wildlife Service, propose to designate
critical habitat for the Zuni bluehead
sucker. If we finalize this rule as
proposed, it would extend the Act’s
protections to this subspecies’ critical
habitat. The effect of these regulations
will be to protect the Zuni bluehead
sucker’s habitat under the Act.
DATES: We will accept comments
received or postmarked on or before
March 26, 2013. Comments submitted
electronically using the Federal
eRulemaking Portal (see ADDRESSES
section, below) must be received by
11:59 p.m. Eastern Time on the closing
date. We must receive requests for
public hearings, in writing, at the
address shown in FOR FURTHER
INFORMATION CONTACT by March 11,
2013.
SUMMARY:
You may submit comments
by one of the following methods:
(1) Electronically: Go to the Federal
eRulemaking Portal: https://
www.regulations.gov. In the Search box,
enter FWS–R2–ES–2013–0002, which is
the docket number for this rulemaking.
Then, in the Search panel on the left
side of the screen, under the Document
Type heading, click on the Proposed
Rules link to locate this document. You
may submit a comment by clicking on
‘‘Comment Now!’’
(2) By hard copy: Submit by U.S. mail
or hand-delivery to: Public Comments
Processing, Attn: FWS–R2–ES–2013–
0002; Division of Policy and Directives
Management; U.S. Fish and Wildlife
Service; 4401 N. Fairfax Drive, MS
2042–PDM; Arlington, VA 22203.
We request that you send comments
only by the methods described above.
We will post all comments on https://
www.regulations.gov. This generally
means that we will post any personal
information you provide us (see the
Public Comments section below for
more information).
ADDRESSES:
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5351
The coordinates or plot points or both
from which the critical habitat maps are
generated are included in the
administrative record for this
rulemaking and are available at https://
www.fws.gov/southwest/es/NewMexico/,
https://www.regulations.gov at Docket
No. FWS–R2–ES–2013–0002, and at the
New Mexico Ecological Services Field
Office (see FOR FURTHER INFORMATION
CONTACT). Any additional tools or
supporting information that we may
develop for this rulemaking will also be
available at the Fish and Wildlife
Service Web site and Field Office set out
above, and may also be included in the
preamble and/or at
www.regulations.gov.
FOR FURTHER INFORMATION CONTACT:
Wally ‘‘J’’ Murphy, Field Supervisor,
U.S. Fish and Wildlife Service, New
Mexico Ecological Services Field Office,
2105 Osuna NE., Albuquerque, NM
87113, by telephone 505–346–2525 or
by facsimile 505–346–2542. Persons
who use a telecommunications device
for the deaf (TDD) may call the Federal
Information Relay Service (FIRS) at
800–877–8339.
SUPPLEMENTARY INFORMATION:
Executive Summary
Why we need to publish a rule. Under
the Act, once a species is determined to
be an endangered or threatened species
throughout all or a significant portion of
its range, we are required to promptly
publish a proposal in the Federal
Register and make a determination on
our proposal within 1 year.
Additionally, critical habitat shall be
designated, to the maximum extent
prudent and determinable, for any
species determined to be an endangered
or threatened species under the Act.
Designations and revisions of critical
habitat can only be completed by
issuing a rule. Elsewhere in today’s
Federal Register, we propose to list the
Zuni bluehead sucker as an endangered
species under the Act.
This rule consists of: A proposed rule
for designation of critical habitat for the
Zuni bluehead sucker. The Zuni
bluehead sucker has been proposed for
listing under the Act. This rule proposes
designation of critical habitat necessary
for the conservation of the species.
The basis for our action. Under the
Act, when a species is proposed for
listing, to the maximum extent prudent
and determinable, we must designate
critical habitat for the species. The
species has been proposed for listing as
endangered, and therefore, we also
propose to designate approximately 472
km (293 mi) of stream habitat as critical
habitat in Apache County, Arizona, and
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Cibola, McKinley, and San Juan
Counties, New Mexico, and on the
Navajo Indian Reservation.
We will seek peer review. We are
seeking comments from knowledgeable
individuals with scientific expertise to
review our analysis of the best available
science and application of that science
and to provide any additional scientific
information to improve this proposed
rule. Because we will consider all
comments and information received
during the comment period, our final
determinations may differ from this
proposal.
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Information Requested
We intend that any final action
resulting from this proposed rule will be
based on the best scientific and
commercial data available and be as
accurate and as effective as possible.
Therefore, we request comments or
information from the public, other
concerned governmental agencies,
Native American tribes, the scientific
community, industry, or any other
interested parties concerning this
proposed rule. We particularly seek
comments concerning:
(1) The reasons why we should or
should not designate habitat as ‘‘critical
habitat’’ under section 4 of the Act (16
U.S.C. 1531 et seq.), including whether
there are threats to the species from
human activity, the degree of which can
be expected to increase due to the
designation, and whether that increase
in threats outweighs the benefit of
designation such that the designation of
critical habitat is not prudent.
(2) Specific information on:
(a) The amount and distribution of the
Zuni bluehead sucker and its habitat;
(b) What may constitute ‘‘physical or
biological features essential to the
conservation of the species,’’ within the
geographical range currently occupied
by the species;
(c) Where these features are currently
found;
(d) Whether any of these features may
require special management
considerations or protection;
(e) What areas, that were occupied at
the time of listing (or are currently
occupied) and that contain features
essential to the conservation of the
species, should be included in the
designation and why; and
(f) What areas not occupied at the
time of listing are essential for the
conservation of the species and why.
(3) Land use designations and current
or planned activities in the areas
occupied by the species or proposed to
be designated as critical habitat, and
possible impacts of these activities on
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this species and proposed critical
habitat.
(4) Information on the projected and
reasonably likely impacts of climate
change on the Zuni bluehead sucker and
proposed critical habitat.
(5) Any foreseeable economic,
national security, or other relevant
impacts that may result from
designating any area that may be
included in the final designation. We
are particularly interested in any
impacts on small entities, and the
benefits of including or excluding areas
from the proposed designation that are
subject to these impacts.
(6) Whether our approach to
designating critical habitat could be
improved or modified in any way to
provide for greater public participation
and understanding, or to assist us in
accommodating public concerns and
comments.
(7) The likelihood of adverse social
reactions to the designation of critical
habitat and how the consequences of
such reactions, if likely to occur, would
relate to the conservation and regulatory
benefits of the proposed critical habitat
designation.
Please include sufficient information
with your submission (such as scientific
journal articles or other publications) to
allow us to verify any scientific or
commercial information you include.
Please note that submissions merely
stating support for or opposition to the
action under consideration without
providing supporting information,
although noted, will not be considered
in making a determination, as section
4(b)(1)(A) of the Act directs that
determinations as to whether any
species is a threatened or endangered
species must be made ‘‘solely on the
basis of the best scientific and
commercial data available.’’
You may submit your comments and
materials concerning this proposed rule
by one of the methods listed in the
ADDRESSES section. We request that you
send comments only by the methods
described in the ADDRESSES section.
If you submit information via https://
www.regulations.gov, your entire
submission—including any personal
identifying information—will be posted
on the Web site. If your submission is
made via a hardcopy that includes
personal identifying information, you
may request at the top of your document
that we withhold this information from
public review. However, we cannot
guarantee that we will be able to do so.
We will post all hardcopy submissions
on https://www.regulations.gov. Please
include sufficient information with your
comments to allow us to verify any
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scientific or commercial information
you include.
Comments and materials we receive,
as well as supporting documentation we
used in preparing this proposed rule,
will be available for public inspection
on https://www.regulations.gov, or by
appointment, during normal business
hours, at the U.S. Fish and Wildlife
Service, New Mexico Ecological
Services Field Office (see FOR FURTHER
INFORMATION CONTACT).
Previous Federal Actions
All previous Federal actions are
described in the proposal to list the
Zuni bluehead sucker as an endangered
species under the Act published
elsewhere in today’s Federal Register.
Critical Habitat Designation for the
Zuni Bluehead Sucker
Background
Critical habitat is defined in section 3
of the Act as:
(1) The specific areas within the
geographical area occupied by the
species, at the time it is listed in
accordance with the Act, on which are
found those physical or biological
features:
(a) Essential to the conservation of the
species, and
(b) Which may require special
management considerations or
protection; and
(2) Specific areas outside the
geographical area occupied by the
species at the time it is listed, upon a
determination that such areas are
essential for the conservation of the
species.
Conservation, as defined under
section 3 of the Act, means to use and
the use of all methods and procedures
that are necessary to bring an
endangered or threatened species to the
point at which the measures provided
pursuant to the Act are no longer
necessary. Such methods and
procedures include, but are not limited
to, all activities associated with
scientific resources management such as
research, census, law enforcement,
habitat acquisition and maintenance,
propagation, live trapping, and
transplantation, and, in the
extraordinary case where population
pressures within a given ecosystem
cannot be otherwise relieved, may
include regulated taking.
Critical habitat receives protection
under section 7 of the Act through the
requirement that Federal agencies
ensure, in consultation with the Service,
that any action they authorize, fund, or
carry out is not likely to result in the
destruction or adverse modification of
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critical habitat. The designation of
critical habitat does not affect land
ownership or establish a refuge,
wilderness, reserve, preserve, or other
conservation area. Such designation
does not allow the government or public
to access private lands. Such
designation does not require
implementation of restoration, recovery,
or enhancement measures by nonFederal landowners. Where a landowner
requests Federal agency funding or
authorization for an action that may
affect a listed species or critical habitat,
the consultation requirements of section
7(a)(2) of the Act would apply, but even
in the event of a destruction or adverse
modification finding, the obligation of
the Federal action agency and the
landowner is not to restore or recover
the species, but to implement
reasonable and prudent alternatives to
avoid destruction or adverse
modification of critical habitat.
Under the first prong of the Act’s
definition of critical habitat, areas
within the geographical area occupied
by the species at the time it was listed
are included in a critical habitat
designation if they contain physical or
biological features (1) essential to the
conservation of the species, and (2)
which may require special management
considerations or protection. For these
areas, critical habitat designations
identify, to the extent known using the
best scientific and commercial data
available, those physical or biological
features essential to the conservation of
the species (such as space, food, cover,
and protected habitat). In identifying
those physical or biological features
within an area, we focus on the
principal biological or physical
constituent elements (primary
constituent elements such as roost sites,
nesting grounds, seasonal wetlands,
water quality, tide, soil type) that are
essential to the conservation of the
species. Primary constituent elements
are those specific elements of the
physical or biological features that
provide for a species’ life-history
processes and are essential to the
conservation of the species.
Under the second prong of the Act’s
definition of critical habitat, we can
designate critical habitat in areas
outside the geographic area occupied by
the species at the time it is listed, upon
a determination that such areas are
essential for the conservation of the
species. For example, an area currently
occupied by the species but that was not
occupied at the time of listing may be
essential to the conservation of the
species and may be included in the
critical habitat designation. We
designate critical habitat in areas
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outside the geographic area occupied by
a species only when a designation
limited to its range would be inadequate
to ensure the conservation of the
species.
Section 4 of the Act requires that we
designate critical habitat on the basis of
the best scientific data available.
Further, our Policy on Information
Standards Under the Endangered
Species Act (published in the Federal
Register on July 1, 1994 (59 FR 34271)),
the Information Quality Act (section 515
of the Treasury and General
Government Appropriations Act for
Fiscal Year 2001 (Pub. L. 106–554; H.R.
5658)), and our associated Information
Quality Guidelines, provide criteria,
establish procedures, and provide
guidance to ensure that our decisions
are based on the best scientific data
available. They require our biologists, to
the extent consistent with the Act and
with the use of the best scientific data
available, to use primary and original
sources of information as the basis for
recommendations to designate critical
habitat.
When we are determining which areas
should be designated as critical habitat,
our primary source of information is
generally the information developed
during the listing process for the
species. Additional information sources
may include the recovery plan for the
species, articles in peer-reviewed
journals, conservation plans developed
by States and counties, scientific status
surveys and studies, biological
assessments, other unpublished
materials, or experts’ opinions or
personal knowledge.
Habitat is dynamic, and species may
move from one area to another over
time. Climate change will be a particular
challenge for biodiversity because the
interaction of additional stressors
associated with climate change and
current stressors may push species
beyond their ability to survive (Lovejoy
2005, pp. 325–326). The synergistic
implications of climate change and
habitat fragmentation are the most
threatening facet of climate change for
biodiversity (Hannah and Lovejoy 2005,
p. 4). Current climate change
predictions for terrestrial areas in the
Northern Hemisphere indicate warmer
air temperatures, more intense
precipitation events, and increased
summer continental drying (Field et al.
1999, pp. 1–3; Hayhoe et al. 2004, p.
12422; Cayan et al. 2005, p. 6;
Intergovernmental Panel on Climate
Change (IPCC) 2007, p. 1181). Climate
change may lead to increased frequency
and duration of severe storms and
droughts (Golladay et al. 2004, p. 504;
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McLaughlin et al. 2002, p. 6074; Cook
et al. 2004, p. 1015).
We recognize that critical habitat
designated at a particular point in time
may not include all of the habitat areas
that we may later determine are
necessary for the recovery of the
species. For these reasons, a critical
habitat designation does not signal that
habitat outside the designated area is
unimportant or may not be needed for
recovery of the species. Areas that are
important to the conservation of the
species, both inside and outside the
critical habitat designation, will
continue to be subject to: (1)
Conservation actions implemented
under section 7(a)(1) of the Act, (2)
regulatory protections afforded by the
requirement in section 7(a)(2) of the Act
for Federal agencies to ensure their
actions are not likely to jeopardize the
continued existence of any endangered
or threatened species, and (3) section 9
of the Act’s prohibitions on taking any
individual of the species, including
taking caused by actions that affect
habitat. Federally funded or permitted
projects affecting listed species outside
their designated critical habitat areas
may still result in jeopardy findings in
some cases. These protections and
conservation tools will continue to
contribute to recovery of this species.
Similarly, critical habitat designations
made on the basis of the best available
information at the time of designation
will not control the direction and
substance of future recovery plans,
habitat conservation plans (HCPs), or
other species conservation planning
efforts if new information available at
the time of these planning efforts calls
for a different outcome.
Prudency Determination
Section 4(a)(3) of the Act, as
amended, and implementing regulations
(50 CFR 424.12), require that, to the
maximum extent prudent and
determinable, the Secretary designate
critical habitat at the time the species is
determined to be an endangered or
threatened species. Our regulations (50
CFR 424.12(a)(1)) state that the
designation of critical habitat is not
prudent when one or both of the
following situations exist: (1) The
species is threatened by taking or other
human activity, and identification of
critical habitat can be expected to
increase the degree of threat to the
species, or (2) such designation of
critical habitat would not be beneficial
to the species.
There is currently no immediate
threat of take attributed to collection or
vandalism under Factor B for this
species, and identification and mapping
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of critical habitat is not expected to
initiate any such threat. In the absence
of finding that the designation of critical
habitat would increase threats to a
species, if there are any benefits to a
critical habitat designation, then a
prudent finding is warranted. Here, the
potential benefits of designation
include: (1) Triggering consultation
under section 7 of the Act, in new areas
for actions in which there may be a
Federal nexus where it would not
otherwise occur because, for example, it
is or has become unoccupied or the
occupancy is in question; (2) focusing
conservation activities on the most
essential features and areas; (3)
providing educational benefits to State
or county governments or private
entities; and (4) preventing people from
causing inadvertent harm to the species.
Therefore, because we have determined
that the designation of critical habitat
will not likely increase the degree of
threat to the species and may provide
some measure of benefit, we find that
designation of critical habitat is prudent
for the Zuni bluehead sucker.
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Critical Habitat Determinability
Having determined that designation is
prudent, under section 4(a)(3) of the
Act, we must find whether critical
habitat for the Zuni bluehead sucker is
determinable. Our regulations at 50 CFR
424.12(a)(2) state that critical habitat is
not determinable when one or both of
the following situations exist:
(i) Information sufficient to perform
required analyses of the impacts of the
designation is lacking, or
(ii) The biological needs of the species
are not sufficiently well known to
permit identification of an area as
critical habitat.
When critical habitat is not
determinable, the Act allows the Service
an additional year to publish a critical
habitat designation (16 U.S.C.
1533(b)(6)(C)(ii)).
We reviewed the available
information pertaining to the biological
needs of the species and habitat
characteristics where the species is
located. This and other information
represent the best scientific data
available and led us to conclude that the
designation of critical habitat is
determinable for the Zuni bluehead
sucker.
Physical or Biological Features
In accordance with section 3(5)(A)(i)
and 4(b)(1)(A) of the Act and regulations
at 50 CFR 424.12, in determining which
areas within the geographic area
occupied by the species at the time of
listing to designate as critical habitat,
we consider the physical or biological
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features that are essential to the
conservation of the species and which
may require special management
considerations or protection. These
include, but are not limited to:
(1) Space for individual and
population growth and for normal
behavior;
(2) Food, water, air, light, minerals, or
other nutritional or physiological
requirements;
(3) Cover or shelter;
(4) Sites for breeding, reproduction, or
rearing (or development) of offspring;
and
(5) Habitats that are protected from
disturbance or are representative of the
historical, geographic, and ecological
distributions of a species.
We derive the specific physical or
biological features required for the Zuni
bluehead sucker from studies of this
species’ habitat, ecology, and life history
as described below. Habitat needs for
specific life stages for Zuni bluehead
sucker have not been described;
therefore, when necessary we will rely
on information available for the
bluehead sucker, which is closely
related to the Zuni bluehead sucker.
Space for Individual and Population
Growth and for Normal Behavior
Zuni bluehead sucker occur in stream
habitats with abundant shade from
overhanging vegetation and boulders, in
pools, runs, and riffles with water
velocities ranging from 0 to 0.35 m/sec
(1.15 ft/sec) or less and ranging in depth
from 0.2–2.0 m (7.9–78.7 in) (Hanson
1980, pp. 34, 42; Propst and Hobbes
1996, pp. 13, 16; Gilbert and Carmen
2011, pp. 8–10). Shade provided by the
overhanging vegetation curtails water
temperature fluctuations in small,
headwater streams, such as those
occupied by Zuni bluehead sucker
(Whitledge et al. 2006, p. 1461).
Substrate in Zuni bluehead sucker
habitat ranges from silt and pebbles to
cobbles, boulders, and bedrock (Hanson
1980, pp. 34, 42; Propst and Hobbes
1996, pp. 13, 16; Gilbert and Carmen
2011, pp. 8–10; NMDGF 2012). Clean
substrate, such as gravel and coarse
sand, free of silt, is necessary for
spawning and egg development
(Maddux and Kepner 1988, p. 364).
Excessive levels of silt can inhibit egg
and juvenile fish development through
the clogging of the small spaces between
substrate particles, which prevents the
free flow of oxygenated water.
Additionally, siltation can reduce the
suitability of the habitat for prey
organisms. Juvenile bluehead sucker
have been found nearshore in slower
and shallower habitats, then moving out
into deeper water and faster flowing
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habitat as they age (Childs et al. 1998,
p. 624).
Water temperatures in occupied
habitats in New Mexico have ranged
from 9.9 to 25.2 degrees Celsius (°C)
(49.8 to 77.3 degrees Fahrenheit (°F))
during survey efforts (Propst et al. 2001,
p. 163; Gilbert and Carmen 2011, pp. 8–
10). Year-round data loggers have
recorded temperatures as low as ¥3.2°C
(24.3 °F) and as high as 24.1°C (75.3 °F)
(Gilbert and Carmen 2011, pp. 8–10).
Therefore, based on the information
above, we identify the following habitat
parameters as the physical or biological
features for the Zuni bluehead sucker:
• A variety of stream habitats,
including riffles, runs, and pools, with
appropriate flows and substrates, with
low to moderate amounts of fine
sediment and substrate embeddedness,
as maintained by natural, unregulated
flow that allows for periodic flooding or,
if flows are modified or regulated, flow
patterns that allow the river to mimic
natural functions, such as flows capable
of transporting sediment.
Food, Water, Air, Light, Minerals, or
Other Nutritional or Physiological
Requirements
Food. The Zuni bluehead sucker is a
benthic forager (eats food from the
stream bottom) that scrapes algae,
insects, and other organic and inorganic
material from the surface of rocks
(NMDGF 2004, p. 8). Stomach content
analysis of Zuni bluehead suckers
revealed small particulate organic
matter, including detritus (nonliving
organic material), algae, small midge
(two-winged fly) larvae, caddisfly
larvae, mayfly larvae, flatworms, and
the occasional small terrestrial insects
(Smith and Koehn 1979, p. 38). In
addition, Smith and Koehn (1979, p. 38)
also found fish scales, snails, and insect
eggs in Zuni bluehead sucker stomachs.
The primary source of food for Zuni
bluehead sucker is periphytic algae
(algae attached to rocks), which occurs
mainly on cobble, boulder, and bedrock
substrates with clean flowing water.
Diet preferences have been described for
adults, but not for the remaining life
stages of Zuni bluehead sucker. Larval
bluehead suckers (<25 mm (approx.1 in)
total length) feed on diatoms (a type of
algae), zooplankton (small floating or
swimming organisms that drift with
water currents), and dipteran larvae
(true fly larvae) in stream areas with low
velocity or in backwater habitats (Muth
and Snyder 1995, p. 100). Juvenile and
adult bluehead sucker are reported
primarily to eat a variety of inorganic
material, organic material, and bottomdwelling insects and other small
organisms (Childs et al. 1998, p. 625;
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Osmundson 1999, p. 28; Brooks et al.
2000, pp. 66–69).
Aquatic invertebrates are another
important component of the Zuni
bluehead sucker diet. These aquatic
invertebrates have specific habitat
requirements of their own. Both
caddisflies and mayflies occur primarily
in a wide variety of standing and
running-water habitats with the greatest
diversity being found in rocky-bottom
streams with an abundance of oxygen
(Merritt and Cummins 1996, pp. 126,
309). Caddisflies and mayflies feed on a
variety of detritus, algae, diatoms, and
macrophytes (aquatic plants) (Merritt
and Cummins 1996, pp. 126, 309).
Habitat that consists of rocky bottoms
with periphytic algal growth is not only
important to sustain aquatic invertebrate
populations (a Zuni bluehead sucker
food source), but also serves as a
primary food resource of the Zuni
bluehead sucker.
Water. As a purely aquatic species,
Zuni bluehead sucker is entirely
dependent on stream habitat for all
stages of their life cycle. Therefore,
perennial flows are an essential feature
with appropriate seasonal flows to
maintain habitat conditions that remove
excess sediments. Areas with
intermittent flows may serve as
connective corridors between occupied
or seasonally occupied habitat through
which the species may move when the
habitat is wetted.
There is very little information on
water quality requirements for Zuni
bluehead sucker. However, excessive
sedimentation is the primary threat to
water quality for the Zuni bluehead
sucker (as discussed above), primarily
due to its effects on reproduction and
food resources. Turbidity (sediment
suspended in the water column) can
inhibit algae production through
reducing sunlight penetration into the
water.
Therefore, based on the information
above, we identify the following prey
base and water quality characteristics as
physical or biological features for the
Zuni bluehead sucker:
• An abundant source of algae
production and an aquatic insect food
base consisting of caddisflies, mayflies,
midges, and various terrestrial insects;
• Streams with no harmful levels of
pollutants;
• Areas devoid of sediment
deposition;
• Perennial flows, or interrupted
stream courses that are periodically
dewatered but that serve as connective
corridors between occupied or
seasonally occupied habitat and through
which the species may move when the
habitat is wetted;
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• Dynamic flows that allow for
periodic changes in channel
morphology.
Cover or Shelter
Cover from predation may be in the
form of deep water or physical
structure. Very little is known about
habitat parameters specifically relating
to cover for Zuni bluehead sucker.
However, during surveys, Zuni
bluehead sucker have been found in
shaded pools and near boulder
outcrops, which may be used for cover
(Kitcheyan 2012, pers. comm.).
Additionally, mature bluehead sucker
are found in deeper water than larvae
and in habitats with less woody cover
than younger life stages, which are more
vulnerable to predation (Childs et al.
1998, p. 624).
Sites for Breeding, Reproduction, or
Rearing (or Development) of Offspring
Zuni bluehead sucker spawn from
early April to early June when water
temperatures are 6 to 15 °C (43 to 59 °F),
peaking around 10 °C (50 °F) (Propst
1999, p. 50; Propst et al. 2001, p. 164).
Zuni bluehead sucker may have two
spawning periods, with the majority of
the spawning effort expended early in
the season (Propst et al. 2001, p. 158).
Females in spawning condition have
been found over gravel beds (Sublette et
al. 1990, p. 210; Propst et al. 2001, p.
158), Clean substrates free of excessive
sedimentation are essential for
successful breeding (see Habitat and
Life History section of our proposed
listing rule published elsewhere in
today’s Federal Register). Periodic
flooding removes excess silt and fine
sand from the stream bottom, breaks up
embedded bottom materials, and
rearranges sediments in ways that
promote algae production and create
suitable habitats with silt-free
substrates.
Therefore, based on the information
above, we identify the following
parameters for breeding, reproduction,
or development of offspring as physical
or biological features for the Zuni
bluehead sucker:
• Gravel and cobble substrates;
• Pool habitat;
• Slower currents along stream
margins with appropriate stream
velocities for larvae;
• Instream flow velocities that are
less than 35 cm/sec (1.1 ft/sec); and
• Dynamic flows that allow for
periodic changes in channel
morphology.
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Habitats Protected From Disturbance or
Representative of the Historical,
Geographic, and Ecological
Distributions of the Species
The Zuni bluehead sucker has a
restricted geographic distribution.
Endemic species (species that are
exclusively native to a particular
location) whose populations exhibit a
high degree of isolation are extremely
susceptible to extinction from both
random and nonrandom catastrophic
natural or human-caused events.
Therefore, it is essential to maintain
both springs and stream systems upon
which the Zuni bluehead sucker
depends. This means protection from
disturbance caused by exposure to land
management actions (logging, cattle
grazing, and road construction), water
contamination, water depletion, beaver
dams, or nonnative species. The Zuni
bluehead sucker must, at a minimum,
sustain its current distribution for the
species to continue to persist.,
Introduced species are a serious threat
to native aquatic species (Miller 1961,
pp. 365, 397–398; Lachner et al. 1970,
p. 21; Ono et al. 1983, pp. 90–91;
Carlson and Muth 1989, pp. 222, 234;
Fuller et al. 1999, p. 1; Propst et al.
2008, pp. 1246–1251; Pilger et al. 2010,
pp. 300, 311–312; see both Factor C:
Disease and Predation, and Factor E:
Other Natural or Manmade Factors
Affecting Its Continued Existence
sections of our proposed listing rule
published elsewhere in today’s Federal
Register). Because the distribution of
the Zuni bluehead sucker is so isolated
and its habitat so restricted,
introduction of certain nonnative
species into its habitat could be
devastating. Potentially harmful
nonnative species include green
sunfish, northern crayfish, fathead
minnow, and other nonnative fisheating fishes.
Zuni bluehead sucker typically
inhabit small desert stream systems
including isolated headwater springs,
small headwater springs, and mainstem
river habitats (Gilbert and Carman 2011,
p. 2) with clean, hard substrate, flowing
water, and abundant riparian vegetation.
Degraded habitat consists of silt-laden
substrates, high turbidity, and deep,
stagnant water (Gilbert and Carman
2011, p. 6). Ponds formed by beaver
dams and impoundments as well as
pools formed during river intermittency
create such degraded habitats.
Therefore, based on the information
above, we identify the necessary
physical or biological features for the
Zuni bluehead sucker:
• Nondegraded habitat devoid of
nonnative aquatic species, or habitat in
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which nonnative aquatic species are at
levels that allow persistence of Zuni
bluehead sucker.
kept nonnatives at a level that allows
the Zuni bluehead sucker to continue to
survive and reproduce.
Primary Constituent Elements for the
Zuni Bluehead Sucker
Under the Act and its implementing
regulations, we are required to identify
the physical or biological features
essential to the conservation of the Zuni
bluehead sucker in areas occupied at the
time of listing, focusing on the features’
primary constituent elements. We
consider primary constituent elements
to be the elements of physical or
biological features that provide for a
species’ life-history processes and are
essential to the conservation of the
species.
Based on our current knowledge of
the physical or biological features and
habitat characteristics required to
sustain the species’ life-history
processes, we determine that the
primary constituent elements specific to
the Zuni bluehead sucker are:
(1) A riverine system with habitat to
support all life stages of Zuni bluehead
sucker (egg, larval, juvenile, and adult),
which includes:
a. Dynamic flows that allow for
periodic changes in channel
morphology and adequate river
functions, such as channel reshaping
and delivery of coarse sediments.
b. Stream courses with perennial
flows, or areas that may be periodically
dewatered but serve as connective
corridors between occupied or
seasonally occupied habitat and through
which the species may move when the
habitat is wetted;
c. Stream microhabitat types
including runs, riffles, and pools with
substrate ranging from gravel, cobble,
and bedrock substrates with low or
moderate amounts of fine sediment and
substrate embeddedness; and
d. Streams with depths generally less
than 2 m (3.3 ft), and with slow to swift
flow velocities less than 35 cm/sec (1.1
ft/sec);
e. Clear, cool water with low turbidity
and temperatures in the general range of
9.0 to 28.0 °C (48.2 to 82.4 °F).
f. No harmful levels of pollutants;
g. Adequate riparian shading to
reduce water temperatures when
ambient temperatures are high and
provide protective cover from predators;
and
(2) An abundant aquatic insect food
base consisting of fine particulate
organic material, filamentous algae,
midge larvae, caddisfly larvae, mayfly
larvae, flatworms, and small terrestrial
insects.
(3) Areas devoid of nonnative aquatic
species or areas that are maintained to
Special Management Considerations or
Protection
When designating critical habitat, we
assess whether the specific areas within
the geographic area occupied by the
species at the time of listing contain
features which are essential to the
conservation of the species and which
may require special management
considerations or protection. We believe
each area included in these designations
requires special management and
protections as described in our unit
descriptions.
We need to consider special
management considerations or
protection for the features essential to
the conservation of the species within
each critical habitat area. The special
management considerations or
protections will depend on the threats
to the essential features in that critical
habitat area. For example, threats
requiring special management
considerations or protection include the
continued spread of nonnative fish
species into Zuni bluehead sucker
habitat or increasing number of beavers
that reduce habitat quality and foster
expansion of nonnative fish and
crayfish. Other threats requiring special
management considerations or
protection include the threat of wildfire
and excessive ash and sediment
following fire. Improper livestock
grazing can be a threat to the remaining
populations of Zuni bluehead sucker
through trampling of habitat and
increasing sedimentation. Inadequate
water quantity resulting from drought
and water withdrawals affect all life
stages of Zuni bluehead sucker.
Additionally, the construction of
impoundments and water diversions
can cause an increase in water depth
behind the structure and a reduction or
elimination of stream habitat below.
We have included below in our
description of each of the critical habitat
areas for the Zuni bluehead sucker a
discussion of the threats occurring in
that area requiring special management
considerations or protection.
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Criteria Used To Identify Critical
Habitat
As required by Section 4(b)(2) of the
Act, we use the best scientific data
available to designate critical habitat.
We review available information
pertaining to the habitat requirements of
the species. In accordance with the Act
and its implementing regulation at 50
CFR 424.12(e), we consider whether
designating additional areas—outside
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those currently occupied as well as
those occupied at the time of listing—
are necessary to ensure the conservation
of the species. We are proposing to
designate critical habitat in areas within
the geographic area occupied by the
species at the time of listing, as
described above in the proposed rule to
list the Zuni bluehead sucker, and that
contain sufficient elements of physical
or biological features to support lifehistory processes essential for the
conservation of the species. We are also
proposing to designate specific areas
outside the geographic area occupied by
the species at the time of listing because
such areas are essential for the
conservation of the species.
Sources of data for this species
include multiple databases maintained
by universities and State agencies for
Arizona and New Mexico, existing State
recovery plans, endangered species
reports, and numerous survey reports on
streams throughout the species’ range
(Sanchez 1975, pp. 1, 4; Propst et al.
1986, pp. 49–51; NMDGF 2003, pp. 6–
10; Sponholtz 2003, pp. 18–22; NMDGF
2004, pp. 1–40; Clarkson and Marsh
2006, pp. 1–2; David 2006, pp. 1–40;
NMDGF 2007, pp. 1–27; Douglas et al.
2009, p. 67; Service 2010, pp. 1–2;
NMDGF 2012; Navajo Nation Heritage
Program 2012, pp. 1–20). We have also
reviewed available information that
pertains to the habitat requirements of
this species. Sources of information on
habitat requirements include existing
State recovery plans, endangered
species reports, studies conducted at
occupied sites and published in peerreviewed articles, agency reports, and
data collected during monitoring efforts
(Propst et al. 2001, pp. 159–161;
NMDGF 2003, pp. 1–14; NMDGF 2004,
pp. 4–7).
The current distribution of the Zuni
bluehead sucker is much reduced from
its historical distribution. We anticipate
that recovery will require continued
protection of existing populations and
habitat, as well as establishing
populations in additional streams that
more closely approximate its historic
distribution in order to ensure there are
adequate numbers of fish in stable
populations and that these populations
occur over a wide geographic area. This
will help to ensure that catastrophic
events, such as wildfire, cannot
simultaneously affect all known
populations.
Areas Occupied at the Time of Listing
The proposed critical habitat
designation does not include all streams
known to have been occupied by the
species historically; instead, it focuses
on occupied streams within the
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historical range that have retained the
necessary PCEs that will allow for the
maintenance and expansion of existing
populations. The following streams
meet the definition of areas occupied by
the species at the time of listing: Agua
Remora, Rio Nutria, Tampico Spring,
Tampico Draw, Kinlichee Creek, Black
Soil Wash, Scattered Willow Wash,
Coyote Wash, Crystal Creek, Sonsela
Creek, Tsaile Creek, Wheatfields Creek,
and Whiskey Creek. There are no
developed areas within the proposed
designation except for barriers
constructed on streams or road crossings
of streams, which do not remove the
suitability of these areas for this species.
Areas Outside of the Geographic Range
at the Time of Listing
The Zuni River, Rio Pescado, Cebolla
Creek, Red Clay Wash, Palisades Creek,
and Little Whiskey Creek are within the
historical range of the Zuni bluehead
sucker but are not within the geographic
range currently occupied by the species;
the Zuni River and Rio Pescado
experience a high degree of river
intermittency, and the Zuni bluehead
sucker has not been seen in Cebolla
Creek, Red Clay Wash, and Little
Whiskey Creek in over 30 years, and it
has not been observed in the Zuni River
or Rio Pescado in approximately 20
years. We consider these sites to be
extirpated. For areas not occupied by
the species at the time of listing, we
must demonstrate that these areas are
essential to the conservation of the
species in order to include them in our
critical habitat designation. To
determine if these areas are essential for
the conservation of the Zuni bluehead
sucker, we considered: (1) The
importance of the site to the overall
status of the species to prevent
extinction and contribute to future
recovery of the Zuni bluehead sucker;
(2) whether the area could be restored
to contain the necessary habitat to
support the Zuni bluehead sucker; (3)
does the site provide connectivity
between occupied sites for genetic
exchange: and (4) whether a population
of the species could be reestablished in
the area.
Of the unoccupied streams, the Zuni
River, Rio Pescado, and Palisades Creek
exhibit varying degrees of intermittency;
the Zuni River and Rio Pescado are
generally only continuous after heavy
flows in the spring (NMDGF 2004, p. 13;
New Mexico Environment Department
(NMED) 2004, p. 1), and Palisades Creek
has been noted as dry during recent
visits (Hobbes 2001, pp. 25–26; Carman
2004, p. 9). However, when the Zuni
River, Rio Pescado, and Cebolla Creek
do exhibit flow and if suitable habitat
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were restored, they could allow for
important population expansion in this
watershed and they are therefore
essential for the conservation of the
Zuni bluehead sucker. On the other
hand, Palisades Creek is a tributary to
Whiskey Creek that, when wetted, likely
does not provide much benefit to the
species. Because this formerly occupied
site has been so severely impacted and,
as a small tributary, it does not connect
occupied sites, it is unlikely to
contribute to the recovery of the species
and is not considered essential to the
conservation of the species. Therefore, it
is not included in the proposed
designation of critical habitat.
In summary, for areas within the
geographic area occupied by the species
at the time of listing, we delineated
critical habitat unit boundaries using
the following criterion:
(1) Evaluate habitat suitability of
stream segments within the geographic
area occupied at the time of listing, and
retain those segments that contain some
or all of the PCEs to support life-history
functions essential for conservation of
the species.
For areas outside the geographic area
occupied by the species at the time of
listing, we delineated critical habitat
unit boundaries using the following
steps:
(2) Evaluate stream segments not
known to have been occupied at listing
but that are within the historical range
of the species (outside of the geographic
area occupied by the species) to
determine if they are essential to the
survival and recovery of the species.
Essential areas are those that:
(a) Serve as an extension of habitat
within the geographic area of an
occupied unit;
(b) Expand the geographic
distribution within areas not occupied
at the time of listing across the historical
range of the species; and
(c) Are connected to other occupied
areas, which will enhance genetic
exchange between populations.
We conclude that the areas proposed
for critical habitat provide for the
conservation of the Zuni bluehead
sucker because they include habitat for
all extant populations and include
habitat for connectivity and dispersal
opportunities within units. Such
opportunities for dispersal assist in
maintaining the population structure
and distribution of the species. The
current amount of habitat that is
occupied is not sufficient for the
recovery of the species; therefore, we
included unoccupied habitat in this
proposed critical habitat designation.
As a final step, we evaluated those
occupied stream segments retained
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5357
through step 1 of the above analysis and
refined the starting and ending points
by evaluating the presence or absence of
appropriate PCEs. We selected upstream
and downstream cutoff points to omit
areas that are highly degraded and are
not likely restorable. For example,
permanently dewatered areas, or areas
in which there was a change to
unsuitable parameters (e.g., water
quality, bedrock substrate) were used to
mark the start or endpoint of a stream
segment proposed for designation.
Critical habitat stream segments were
then mapped using ArcMap version 10
(Environmental Systems Research
Institute, Inc.), a Geographic
Information Systems program.
The areas proposed for designation as
critical habitat provide sufficient stream
and spring habitat for breeding,
nonbreeding, and dispersing adult Zuni
bluehead sucker, as well as for the
habitat needs for juvenile and larval
stages of this fish. In general, the PCEs
of critical habitat are contained within
the riverine ecosystem formed by the
wetted channel and the adjacent
floodplains within 91.4 lateral m (300
lateral ft) on either side of bankfull
stage, except where bounded by canyon
walls. Areas within the lateral extent
also contribute to the PCEs, including
water quality and intermittent areas
through which fish may move when
wetted. Zuni bluehead sucker use the
riverine ecosystem for feeding, breeding,
and sheltering while breeding and
migrating.
When determining proposed critical
habitat boundaries, we made every
effort to avoid including developed
areas such as lands covered by bridges,
docks, aqueducts, and other structures
because such lands lack physical or
biological features for the Zuni bluehead
sucker. The scale of the maps we
prepared under the parameters for
publication within the Code of Federal
Regulations may not reflect the
exclusion of such developed lands. Any
such lands inadvertently left inside
critical habitat boundaries shown on the
maps of this proposed rule have been
excluded by text in the proposed rule
and are not proposed for designation as
critical habitat. Therefore, if the critical
habitat is finalized as proposed, a
Federal action involving these lands
would not trigger section 7 consultation
with respect to critical habitat and the
requirement of no adverse modification
unless the specific action would affect
the physical or biological features in the
adjacent critical habitat.
We are proposing for designation of
critical habitat lands that we have
determined are occupied at the time of
listing and contain sufficient elements
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of physical or biological features to
support life-history processes essential
for the conservation of the species, and
lands outside of the geographic area
occupied at the time of listing that we
have determined are essential for the
conservation of the Zuni bluehead
sucker.
Segments were proposed for
designation based on sufficient elements
of physical or biological features being
present to support the Zuni bluehead
sucker life-history processes. Some
segments contained all of the identified
elements of physical or biological
features and supported multiple lifehistory processes. Some segments
contained only some elements of the
physical or biological features necessary
to support the Zuni bluehead sucker’s
particular use of that habitat.
The critical habitat designation is
defined by the map or maps, as
modified by any accompanying
regulatory text, presented at the end of
this document in the rule portion. We
include more detailed information on
the boundaries of the critical habitat
designation in the preamble of this
document. We will make the
coordinates or plot points or both on
which each map is based available to
the public on https://
www.regulations.gov at Docket No.
FWS–R2–ES–2012–0101, on our
Internet sites https://www.fws.gov/
southwest/es/NewMexico/, and at the
field office responsible for the
designation (see FOR FURTHER
INFORMATION CONTACT above).
Proposed Critical Habitat Designation
We are proposing to designate
approximately 472 km (293 mi) in three
units as critical habitat for the Zuni
bluehead sucker. The critical habitat
areas we describe below constitute our
current best assessment of areas that
meet the definition of critical habitat for
Zuni bluehead sucker. The three areas
we propose as critical habitat are: (1)
Zuni River Unit; (2) Kinlichee Creek
Unit; and (3) San Juan River Unit. Table
1 shows the occupancy of the units, the
land ownership, and approximate areas
of the proposed designated areas for the
Zuni bluehead sucker.
TABLE 1—PROPOSED CRITICAL HABITAT UNITS FOR ZUNI BLUEHEAD SUCKER
[Area estimates reflect all land within critical habitat unit boundaries]
Stream segment
Occupied at the time of listing
Land ownership
Length of unit
in kilometers
(miles)
Unit 1—Zuni River Unit
Subunit 1a—Zuni River Headwaters
Agua Remora ...........................................
Yes ..........................................................
Yes ..........................................................
Forest Service .........................................
Private .....................................................
Zuni Pueblo .............................................
Forest Service .........................................
State of New Mexico ...............................
Private .....................................................
Forest Service .........................................
Private .....................................................
Private .....................................................
6.6 (4.1)
2.4 (1.5)
38.9 (24.2)
4.1 (2.6)
1.8 (1.1)
14.2 (8.8)
2.3 (1.4)
3.7 (2.3)
0.2 (0.1)
Rio Nutria .................................................
Yes ..........................................................
Tampico Draw ..........................................
Yes ..........................................................
Tampico Spring ........................................
Total ..................................................
..................................................................
..................................................................
74.2 (46.1)
Subunit 1b—Zuni River Mainstem
Zuni River .................................................
Rio Pescado .............................................
No ............................................................
No ............................................................
No ............................................................
Zuni Pueblo .............................................
Zuni Pueblo .............................................
State of New Mexico ...............................
Private .....................................................
Zuni Pueblo .............................................
State of New Mexico ...............................
Forest Service .........................................
Private .....................................................
7.4 (4.6)
47.3 (29.4)
5.8 (3.6)
15.4 (9.6)
3.7 (2.3)
0.4 (.02)
6.4 (4.0)
21.4 (13.3)
Cebolla Creek ..........................................
Total ..................................................
..................................................................
..................................................................
107.8 (67.0)
Unit 2—Kinlichee Creek Unit
Subunit 2a—Kinlichee Creek
Black Soil Wash .......................................
Kinlichee Creek ........................................
Scattered Willow Wash ............................
Yes ..........................................................
Yes ..........................................................
Yes ..........................................................
Navajo Nation ..........................................
Navajo Nation ..........................................
Navajo Nation ..........................................
21.6 (13.4)
47.1 (29.3)
18.2 (11.3)
Total ..................................................
..................................................................
..................................................................
86.9 (54.0)
Subunit 2b—Red Clay Wash
sroberts on DSK5SPTVN1PROD with
Red Clay Wash ........................................
No ............................................................
Navajo Nation ..........................................
9.6 (6.0)
Unit 3—San Juan River Unit
Subunit 3a—Canyon de Chelly
Coyote Wash ............................................
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Yes ..........................................................
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Navajo Nation * ........................................
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5359
TABLE 1—PROPOSED CRITICAL HABITAT UNITS FOR ZUNI BLUEHEAD SUCKER—Continued
[Area estimates reflect all land within critical habitat unit boundaries]
Stream segment
Occupied at the time of listing
Land ownership
Crystal Creek ...........................................
Yes ..........................................................
Sonsela Creek ..........................................
Tsaile Creek .............................................
Yes ..........................................................
Yes ..........................................................
Wheatfields Creek ....................................
Yes ..........................................................
Whiskey Creek .........................................
Yes ..........................................................
Total ..................................................
..................................................................
Navajo
Navajo
Navajo
Navajo
Navajo
Navajo
Navajo
Navajo
Navajo
Length of unit
in kilometers
(miles)
Nation * ........................................
Nation ..........................................
Nation * ........................................
Nation * ........................................
Nation ..........................................
Nation * ........................................
Nation ..........................................
Nation * ........................................
Nation ..........................................
0.5 (0.3)
34.2 (21.2)
19.5 (12.1)
23.0 (14.3)
30.6 (19.0)
8.5 (5.3)
29.3 (18.2)
7.5 (4.7)
28.1 (17.5)
..................................................................
187.9 (112.7)
Subunit 3b—Little Whiskey Creek
Little Whiskey Creek ................................
No ............................................................
Navajo Nation ..........................................
8.9 (5.5)
Total ..................................................
..................................................................
..................................................................
8.9 (5.5)
* These lands are managed by National Park Service in trust for the Navajo Nation.
Note: Area sizes may not sum due to rounding.
We present below brief descriptions
of the units and reasons why the units
meet the definition of critical habitat for
the Zuni bluehead sucker.
sroberts on DSK5SPTVN1PROD with
Unit 1: Zuni River Unit
Subunit 1a—Zuni River Headwaters:
Subunit 1a consists of 74.2 km (46.1 mi)
along Agua Remora, Rio Nutria,
Tampico Draw, and Tampico Spring in
McKinley County, New Mexico. The
land in this subunit is primarily owned
by Zuni Pueblo, Forest Service, and
private landowners with a small amount
of State inholdings. The Zuni bluehead
sucker occupies all stream reaches in
this subunit, and the subunit contains
all of the primary constituent elements
of the physical or biological features
essential to the conservation of the Zuni
bluehead sucker. This unit represents
the only remaining headwater spring
habitats occupied by Zuni bluehead
sucker.
Livestock grazing is primarily
regulated by the Forest Service and Zuni
Pueblo in this subunit; however,
trespass livestock grazing may occur.
Additional special management
considerations or protection may be
required within Subunit 1a to address
low water levels as a result of water
withdrawals and drought, predation
from nonnative green sunfish, and the
upstream and downstream effects of
impoundments. Such special
management or protection may include
maintaining instream flows, nonnative
species removal, and reservoir
management that improves up- and
downstream habitat to benefit the Zuni
bluehead sucker.
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Subunit 1b—Zuni River Mainstem:
Subunit 1b consists of 107.8 km (67.0
mi) of potential Zuni bluehead sucker
habitat along the Zuni River, Rio
Pescado, and Cebolla Creek in McKinley
and Cibola Counties, New Mexico. Land
within this subunit is primarily owned
by Zuni Pueblo and private landowners,
with a small amount of Forest Service
and State land. The Zuni bluehead
sucker historically occupied these
streams but has not been found in the
Zuni River or Rio Pescado since the
mid-1990s (NMDGF 2004, p. 5) and has
been extirpated from Cebolla Creek
since at least 1979 (Hanson 1980, pp.
29, 34). We consider this unit
unoccupied. When wetted and if
suitable habitat were present, the Zuni
River and Rio Pescado could provide
important connections between
occupied reaches in Subunit 1a and
potential future populations in Cebolla
Creek, which has been identified as
containing suitable habitat in the past
and could provide for significant
population expansion. Therefore, this
subunit is essential for the conservation
of the Zuni bluehead sucker because it
provides for connection between
populations and also provides space for
the growth and expansion of the species
in this portion of its historical range.
Unit 2: Kinlichee Creek Unit
Subunit 2a—Kinlichee Creek: Subunit
2a consists of 86.9 km (54.0 mi) along
Kinlichee Creek and two tributaries
(Black Soil Wash and Scattered Willow
Wash) in Apache County, Arizona. This
entire subunit is located within the
Navajo Indian Reservation. The Zuni
bluehead sucker occupies all stream
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reaches in this subunit, and the subunit
contains all of the primary constituent
elements of the physical or biological
features essential to the conservation of
the Zuni bluehead sucker.
Special management considerations
or protection may be required within
Subunit 2a to address low water levels
as a result of water withdrawals and
drought, sedimentation and riparian
vegetation destruction from road
development and livestock grazing, and
predation from nonnative species. Such
special management considerations or
protection may include instream flows,
stream fencing, erosion control
structures along roads and during
construction, reservoir management that
improves up- and downstream habitat to
benefit the Zuni bluehead sucker and
nonnative species removal.
Subunit 2b—Red Clay Wash: Subunit
2b consists of 9.6 km (6.0 mi) of
potential Zuni bluehead sucker habitat
along Red Clay Wash, in Apache
County, Arizona, on the Navajo Indian
Reservation. The Zuni bluehead sucker
historically occupied this stream but
does not currently occur there.
Inclusion of Red Clay Wash expands the
recovery potential of the Zuni bluehead
sucker in the lower Kinlichee watershed
by increasing population redundancy
within the species’ historical range and
is therefore essential to the conservation
of the species.
Unit 3: San Juan River Unit
Subunit 3a—Canyon de Chelly:
Subunit 3a consists of 187.9 km (112.7
mi) along Tsaile Creek, Wheatfields
Creek, Whiskey Creek, Coyote Wash,
Crystal Creek, and Sonsela Creek in
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Apache County, Arizona, and San Juan
County, New Mexico. This unit is
located within the Navajo Indian
Reservation, portions of which are
managed by the National Park Service as
Canyon de Chelly National Monument
in trust for the Navajo Nation. The Zuni
bluehead sucker occupies all stream
reaches in this subunit, and the subunit
contains all of the primary constituent
elements of the physical or biological
features essential to the conservation of
the Zuni bluehead sucker.
Special management considerations
or protection may be required within
Subunit 3a to address low water levels
as a result of water withdrawals and
drought, sedimentation and riparian
vegetation destruction from road
development and livestock grazing, and
predation from nonnative species. Such
special management considerations or
protection may include instream flows
stream fencing, erosion control
structures along roads and during
construction, reservoir management that
improves up- and downstream habitat to
benefit the Zuni bluehead sucker, and
nonnative species removal.
Subunit 3b—Little Whiskey Creek:
Subunit 3b consists of 8.9 km (5.5 mi)
of potential Zuni bluehead sucker
habitat along Little Whiskey Creek in
San Juan County, New Mexico, on the
Navajo Indian Reservation. The Zuni
bluehead sucker does not currently
occur in Little Whiskey Creek, but
suitable habitat is present and it is
reasonable to conclude the species
occurred there historically. Inclusion of
Little Whiskey Creek expands the
recovery potential of the Zuni bluehead
sucker in the upper Whiskey Creek
watershed by increasing population
redundancy within the species’
historical range and is therefore
essential to the conservation of the
species.
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Effects of Critical Habitat Designation
Section 7 Consultation
Section 7(a)(2) of the Act requires
Federal agencies, including the Service,
to ensure that any action they fund,
authorize, or carry out is not likely to
jeopardize the continued existence of
any endangered species or threatened
species or result in the destruction or
adverse modification of designated
critical habitat of such species. In
addition, section 7(a)(4) of the Act
requires Federal agencies to confer with
the Service on any agency action which
is likely to jeopardize the continued
existence of any species proposed to be
listed under the Act or result in the
destruction or adverse modification of
proposed critical habitat.
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Decisions by the 5th and 9th Circuit
Courts of Appeals have invalidated our
regulatory definition of ‘‘destruction or
adverse modification’’ (50 CFR 402.02)
(see Gifford Pinchot Task Force v. U.S.
Fish and Wildlife Service, 378 F. 3d
1059 (9th Cir. 2004) and Sierra Club v.
U.S. Fish and Wildlife Service et al., 245
F.3d 434, 442 (5th Cir. 2001)), and we
do not rely on this regulatory definition
when analyzing whether an action is
likely to destroy or adversely modify
critical habitat. Under the statutory
provisions of the Act, we determine
destruction or adverse modification on
the basis of whether, with
implementation of the proposed Federal
action, the affected critical habitat
would continue to serve its intended
conservation role for the species.
If a Federal action may affect a listed
species or its critical habitat, the
responsible Federal agency (action
agency) must enter into consultation
with us. Examples of actions that are
subject to the section 7 consultation
process are actions on State, tribal,
local, or private lands that require a
Federal permit (such as a permit from
the U.S. Army Corps of Engineers under
section 404 of the Clean Water Act (33
U.S.C. 1251 et seq.) or a permit from the
Service under section 10 of the Act) or
that involve some other Federal action
(such as funding from the Federal
Highway Administration, Federal
Aviation Administration, or the Federal
Emergency Management Agency).
Federal actions not affecting listed
species or critical habitat, and actions
on State, tribal, local, or private lands
that are not federally funded or
authorized, do not require section 7
consultation.
As a result of section 7 consultation,
we document compliance with the
requirements of section 7(a)(2) through
our issuance of:
(1) A concurrence letter for Federal
actions that may affect, but are not
likely to adversely affect, listed species
or critical habitat; or
(2) A biological opinion for Federal
actions that may affect and are likely to
adversely affect listed species or critical
habitat.
When we issue a biological opinion
concluding that a project is likely to
jeopardize the continued existence of a
listed species and/or destroy or
adversely modify critical habitat, we
provide reasonable and prudent
alternatives to the project, if any are
identifiable, that would avoid the
likelihood of jeopardy and/or
destruction or adverse modification of
critical habitat. We define ‘‘reasonable
and prudent alternatives’’ (at 50 CFR
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402.02) as alternative actions identified
during consultation that:
(1) Can be implemented in a manner
consistent with the intended purpose of
the action,
(2) Can be implemented consistent
with the scope of the Federal agency’s
legal authority and jurisdiction,
(3) Are economically and
technologically feasible, and
(4) Would, in the Director’s opinion,
avoid the likelihood of jeopardizing the
continued existence of the listed species
and/or avoid the likelihood of
destroying or adversely modifying
critical habitat.
Reasonable and prudent alternatives
can vary from slight project
modifications to extensive redesign or
relocation of the project. Costs
associated with implementing a
reasonable and prudent alternative are
similarly variable.
Regulations at 50 CFR 402.16 require
Federal agencies to reinitiate
consultation on previously reviewed
actions in instances where we have
listed a new species or subsequently
designated critical habitat that may be
affected and the Federal agency has
retained discretionary involvement or
control over the action (or the agency’s
discretionary involvement or control is
authorized by law). Consequently,
Federal agencies sometimes may need to
request reinitiation of consultation with
us on actions for which formal
consultation has been completed, if
those actions with discretionary
involvement or control may affect
subsequently listed species or
designated critical habitat.
Application of the ‘‘Adverse
Modification’’ Standard
The key factor related to the adverse
modification determination is whether,
with implementation of the proposed
Federal action, the affected critical
habitat would continue to serve its
intended conservation role for the
species. Activities that may destroy or
adversely modify critical habitat are
those that alter the physical or
biological features to an extent that
appreciably reduces the conservation
value of critical habitat for the Zuni
bluehead sucker. As discussed above,
the role of critical habitat is to support
life-history needs of the species and
provide for the conservation of the
species.
Section 4(b)(8) of the Act requires us
to briefly evaluate and describe, in any
proposed or final regulation that
designates critical habitat, activities
involving a Federal action that may
destroy or adversely modify such
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habitat, or that may be affected by such
designation.
Activities that may affect critical
habitat, when carried out, funded, or
authorized by a Federal agency, should
result in consultation for the Zuni
bluehead sucker. These activities
include, but are not limited to:
(1) Actions that would diminish flows
within the active stream channel. Such
activities could include, but are not
limited to: Water diversion, water
withdrawal, channelization,
construction of any barriers or
impediments within the active stream
channel, construction of permanent or
temporary diversion structures, and
groundwater pumping within aquifers
associated with the stream or springs.
These activities could affect water
depth, velocity, and flow patterns, all of
which are essential to the different life
stages of Zuni bluehead sucker.
(2) Actions that would significantly
increase sediment deposition within a
stream channel. Such activities could
include, but are not limited to:
Excessive sedimentation from livestock
grazing, road construction, commercial
or urban development, channel
alteration, timber harvest, or other
watershed and floodplain disturbances.
These activities could adversely affect
reproduction of the species by
preventing hatching of eggs through
suffocation, or by eliminating suitable
habitat for egg placement by Zuni
bluehead sucker. In addition, excessive
levels of sedimentation reduce or
eliminate algae production and can
make it difficult for the Zuni bluehead
sucker to locate prey.
(3) Actions that result in the
introduction, spread, or augmentation of
nonnative aquatic species in occupied
stream segments, or in stream segments
that are hydrologically connected to
occupied stream segments, even if those
segments are occasionally intermittent,
or introduction of other species that
compete with or prey on Zuni bluehead
sucker. Possible actions could include,
but are not limited to: Stocking of
nonnative fishes, stocking of sport fish,
or other related actions. These activities
can introduce parasites or disease, or
affect the growth, reproduction, and
survival of Zuni bluehead sucker.
(4) Actions that would significantly
alter channel morphology. Such
activities could include, but are not
limited to: Channelization,
impoundment, road and bridge
construction, mining, dredging, and
destruction of riparian vegetation. These
activities may lead to changes in water
flows and levels that would degrade or
eliminate the Zuni bluehead, their
habitats, or both. These actions can also
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lead to increased sedimentation and
degradation of the water.
(5) Actions that significantly alter the
water chemistry of the active channel.
Such activities could include release of
chemicals, biological pollutants, or
other substances into the surface water
or connected groundwater at a point
source or by dispersed release (nonpoint
source), and storage of chemicals or
pollutants that can be transmitted, via
surface water, groundwater, or air, into
critical habitat. These actions can affect
water chemistry and the prey base of the
Zuni bluehead sucker.
Exemptions
Application of Section 4(a)(3) of the Act
The Sikes Act Improvement Act of
1997 (Sikes Act) (16 U.S.C. 670a)
required each military installation that
includes land and water suitable for the
conservation and management of
natural resources to complete an
integrated natural resources
management plan (INRMP) by
November 17, 2001. An INRMP
integrates implementation of the
military mission of the installation with
stewardship of the natural resources
found on the base. Each INRMP
includes:
(1) An assessment of the ecological
needs on the installation, including the
need to provide for the conservation of
listed species;
(2) A statement of goals and priorities;
(3) A detailed description of
management actions to be implemented
to provide for these ecological needs;
and
(4) A monitoring and adaptive
management plan.
Among other things, each INRMP
must, to the extent appropriate and
applicable, provide for fish and wildlife
management; fish and wildlife habitat
enhancement or modification; wetland
protection, enhancement, and
restoration where necessary to support
fish and wildlife; and enforcement of
applicable natural resource laws.
The National Defense Authorization
Act for Fiscal Year 2004 (Pub. L. 108–
136) amended the Act to limit areas
eligible for designation as critical
habitat. Specifically, section 4(a)(3)(B)(i)
of the Act (16 U.S.C. 1533(a)(3)(B)(i))
now provides: ‘‘The Secretary shall not
designate as critical habitat any lands or
other geographic areas owned or
controlled by the Department of
Defense, or designated for its use, that
are subject to an integrated natural
resources management plan prepared
under section 101 of the Sikes Act (16
U.S.C. 670a), if the Secretary determines
in writing that such plan provides a
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5361
benefit to the species for which critical
habitat is proposed for designation.’’
There are no Department of Defense
lands within the proposed critical
habitat designation for Zuni bluehead
sucker.
Exclusions
Application of Section 4(b)(2) of the Act
Section 4(b)(2) of the Act states that
the Secretary shall designate and make
revisions to critical habitat on the basis
of the best available scientific data after
taking into consideration the economic
impact, national security impact, and
any other relevant impact of specifying
any particular area as critical habitat.
The Secretary may exclude an area from
critical habitat if he determines that the
benefits of such exclusion outweigh the
benefits of specifying such area as part
of the critical habitat, unless he
determines, based on the best scientific
data available, that the failure to
designate such area as critical habitat
will result in the extinction of the
species. In making that determination,
the statute on its face, as well as the
legislative history, are clear that the
Secretary has broad discretion regarding
which factor(s) to use and how much
weight to give to any factor.
Under section 4(b)(2) of the Act, we
may exclude an area from designated
critical habitat based on economic
impacts, impacts on national security,
or any other relevant impacts. In
considering whether to exclude a
particular area from the designation, we
identify the benefits of including the
area in the designation, identify the
benefits of excluding the area from the
designation, and evaluate whether the
benefits of exclusion outweigh the
benefits of inclusion. If the analysis
indicates that the benefits of exclusion
outweigh the benefits of inclusion, the
Secretary may exercise his discretion to
exclude the area only if such exclusion
would not result in the extinction of the
species.
Exclusions Based on Economic Impacts
Under section 4(b)(2) of the Act, we
consider the economic impacts of
specifying any particular area as critical
habitat. In order to consider economic
impacts, we are preparing an analysis of
the economic impacts of the proposed
critical habitat designation and related
factors. Potential land use sectors that
may be affected by the Zuni bluehead
sucker critical habitat designation
include water diversion or
impoundment repairs, forest
management (silvicultural practices),
fire suppression activities, road
development, grazing, groundwater
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withdrawals, and subdivision
development. We also consider any
social impacts that might occur because
of the designation.
During the development of a final
designation, we will consider economic
impacts based on information in our
economic analysis, public comments,
and other new information, and areas
may be excluded from the final critical
habitat designation under section 4(b)(2)
of the Act and our implementing
regulations at 50 CFR 424.19.
Exclusions Based on National Security
Impacts
Under section 4(b)(2) of the Act, we
consider whether there are lands where
a national security impact might exist.
In preparing this proposal, we have
determined that the lands within the
proposed designation of critical habitat
for the Zuni bluehead sucker are not
owned or managed by the Department of
Defense, and, therefore, we anticipate
no impact on national security.
Consequently, the Secretary is not
intending to exercise his discretion to
exclude any areas from the final
designation based on impacts on
national security.
sroberts on DSK5SPTVN1PROD with
Exclusions Based on Other Relevant
Impacts
Under section 4(b)(2) of the Act, we
consider any other relevant impacts, in
addition to economic impacts and
impacts on national security. We
consider a number of factors including
whether the landowners have developed
any HCPs or other management plans
for the area, or whether there are
conservation partnerships that would be
encouraged by designation of, or
exclusion from, critical habitat. In
addition, we look at any tribal issues,
and consider the government-togovernment relationship of the United
States with tribal entities. We also
consider any social impacts that might
occur because of the designation.
When we evaluate the existence of a
conservation plan when considering the
benefits of exclusion, we consider a
variety of factors, including but not
limited to, whether the plan is finalized;
how it provides for the conservation of
the essential physical or biological
features; whether there is a reasonable
expectation that the conservation
management strategies and actions
contained in a management plan will be
implemented into the future; whether
the conservation strategies in the plan
are likely to be effective; and whether
the plan contains a monitoring program
or adaptive management to ensure that
the conservation measures are effective
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and can be adapted in the future in
response to new information.
There are tribal lands included in the
proposed designation of critical habitat
for the Zuni bluehead sucker. Using the
criteria found in the Criteria Used To
Identify Critical Habitat section, we
have determined that tribal lands that
are occupied by the Zuni bluehead
sucker contain the features essential for
the conservation the species, as well as
tribal lands unoccupied by the Zuni
bluehead sucker that are essential for
the conservation of the species. We have
begun government-to-government
consultation with these tribes, and will
continue to do so throughout the public
comment period and during
development of the final designation of
critical habitat for the Zuni bluehead
sucker. We will consider these areas for
exclusion from the final critical habitat
designation to the extent consistent with
the requirements of section 4(b)(2) of the
Act. The Navajo Nation and Zuni
Pueblo are the main tribes affected by
this proposed rule. We sent notification
letters in July 2012 to both tribes
describing the exclusion process under
section 4(b)(2) of the Act, and we have
engaged in conversations with both
tribes about the proposal to the extent
possible without disclosing
predecisional information. We
coordinated with the Navajo Nation in
May 2012, to coordinate surveys on
Navajo lands. Additionally, we are
working with Zuni Pueblo to develop a
management plan for their lands. We
will schedule a meeting with the tribes
and any other interested tribes shortly
after publication of this proposed rule
so that we can give them as much time
as possible to comment.
A final determination on whether the
Secretary will exercise his discretion to
exclude any of these areas from critical
habitat for the Zuni bluehead sucker
will be made when we publish the final
rule designating critical habitat. We will
take into account public comments and
carefully weigh the benefits of exclusion
versus inclusion of these areas. We may
also consider areas not identified above
for exclusion from the final critical
habitat designation based on
information we may receive during the
preparation of the final rule (e.g.,
management plans for additional areas).
Peer Review
In accordance with our joint policy on
peer review published in the Federal
Register on July 1, 1994 (59 FR 34270),
we will seek the expert opinions of at
least three appropriate and independent
specialists regarding this proposed rule.
The purpose of peer review is to ensure
that our listing determination and
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critical habitat designation are based on
scientifically sound data, assumptions,
and analyses. We have invited these
peer reviewers to comment during this
public comment period.
We will consider all comments and
information received during this
comment period on this proposed rule
during our preparation of a final
determination. Accordingly, the final
decision may differ from this proposal.
Public Hearings
Section 4(b)(5) of the Act provides for
one or more public hearings on this
proposal, if requested. Requests must be
received within 45 days after the date of
publication of this proposed rule in the
Federal Register. Such requests must be
sent to the address shown in the FOR
FURTHER INFORMATION CONTACT section.
We will schedule public hearings on
this proposal, if any are requested, and
announce the dates, times, and places of
those hearings, as well as how to obtain
reasonable accommodations, in the
Federal Register and local newspapers
at least 15 days before the hearing.
Required Determinations
Regulatory Planning and Review—
Executive Orders 12866 and 13563
Executive Order 12866 provides that
the Office of Information and Regulatory
Affairs will review all significant rules.
The Office of Information and
Regulatory Affairs has determined that
this rule is not significant.
Executive Order 13563 reaffirms the
principles of Executive Order 12866
while calling for improvements in the
nation’s regulatory system to promote
predictability, to reduce uncertainty,
and to use the best, most innovative,
and least burdensome tools for
achieving regulatory ends. The
executive order directs agencies to
consider regulatory approaches that
reduce burdens and maintain flexibility
and freedom of choice for the public
where these approaches are relevant,
feasible, and consistent with regulatory
objectives. Executive Order 13563
emphasizes further that regulations
must be based on the best available
science and that the rulemaking process
must allow for public participation and
an open exchange of ideas. We have
developed this rule in a manner
consistent with these requirements.
Regulatory Flexibility Act (5 U.S.C. 601
et seq.)
Under the Regulatory Flexibility Act
(RFA; 5 U.S.C. 601 et seq.) as amended
by the Small Business Regulatory
Enforcement Fairness Act (SBREFA) of
1996 (5 U.S.C 801 et seq.), whenever an
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agency must publish a notice of
rulemaking for any proposed or final
rule, it must prepare and make available
for public comment a regulatory
flexibility analysis that describes the
effects of the rule on small entities
(small businesses, small organizations,
and small government jurisdictions).
However, no regulatory flexibility
analysis is required if the head of the
agency certifies the rule will not have a
significant economic impact on a
substantial number of small entities.
The SBREFA amended the RFA to
require Federal agencies to provide a
certification statement of the factual
basis for certifying that the rule will not
have a significant economic impact on
a substantial number of small entities.
According to the Small Business
Administration, small entities include
small organizations such as
independent nonprofit organizations;
small governmental jurisdictions,
including school boards and city and
town governments that serve fewer than
50,000 residents; and small businesses
(13 CFR 121.201). Small businesses
include such businesses as
manufacturing and mining concerns
with fewer than 500 employees,
wholesale trade entities with fewer than
100 employees, retail and service
businesses with less than $5 million in
annual sales, general and heavy
construction businesses with less than
$27.5 million in annual business,
special trade contractors doing less than
$11.5 million in annual business, and
forestry and logging operations with
fewer than 500 employees and annual
business less than $7 million. To
determine whether small entities may
be affected, we will consider the types
of activities that might trigger regulatory
impacts under this designation as well
as types of project modifications that
may result. In general, the term
‘‘significant economic impact’’ is meant
to apply to a typical small business
firm’s business operations.
Importantly, the incremental impacts
of a rule must be both significant and
substantial to prevent certification of the
rule under the RFA and to require the
preparation of an initial regulatory
flexibility analysis. If a substantial
number of small entities are affected by
the proposed critical habitat
designation, but the per-entity economic
impact is not significant, the Service
may certify. Likewise, if the per-entity
economic impact is likely to be
significant, but the number of affected
entities is not substantial, the Service
may also certify.
The Service’s current understanding
of recent case law is that Federal
agencies are only required to evaluate
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the potential impacts of rulemaking on
those entities directly regulated by the
rulemaking; therefore, they are not
required to evaluate the potential
impacts to those entities not directly
regulated. The designation of critical
habitat for an endangered or threatened
species only has a regulatory effect
where a Federal action agency is
involved in a particular action that may
affect the designated critical habitat.
Under these circumstances, only the
Federal action agency is directly
regulated by the designation, and,
therefore, consistent with the Service’s
current interpretation of RFA and recent
case law, the Service may limit its
evaluation of the potential impacts to
those identified for Federal action
agencies. Under this interpretation,
there is no requirement under the RFA
to evaluate the potential impacts to
entities not directly regulated, such as
small businesses. However, Executive
Orders 12866 and 13563 direct Federal
agencies to assess costs and benefits of
available regulatory alternatives in
quantitative (to the extent feasible) and
qualitative terms. Consequently, it is the
current practice of the Service to assess
to the extent practicable these potential
impacts if sufficient data are available,
whether or not this analysis is believed
by the Service to be strictly required by
the RFA. In other words, while the
effects analysis required under the RFA
is limited to entities directly regulated
by the rulemaking, the effects analysis
under the Act, consistent with the EO
regulatory analysis requirements, can
take into consideration impacts to both
directly and indirectly impacted
entities, where practicable and
reasonable.
In conclusion, we believe that, based
on our interpretation of directly
regulated entities under the RFA and
relevant case law, this designation of
critical habitat will only directly
regulate Federal agencies which are not
by definition small business entities.
And as such, we certify that, if
promulgated, this designation of critical
habitat would not have a significant
economic impact on a substantial
number of small business entities.
Therefore, an initial regulatory
flexibility analysis is not required.
However, though not necessarily
required by the RFA, in our draft
economic analysis for this proposal we
will consider and evaluate the potential
effects to third parties that may be
involved with consultations with
Federal action agencies related to this
action.
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Energy Supply, Distribution, or Use—
Executive Order 13211
Executive Order 13211 (Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use) requires agencies
to prepare Statements of Energy Effects
when undertaking certain actions. We
do not expect the designation of this
proposed critical habitat to significantly
affect energy supplies, distribution, or
use. Therefore, this action is not a
significant energy action, and no
Statement of Energy Effects is required.
However, we will further evaluate this
issue as we conduct our economic
analysis, and review and revise this
assessment as warranted.
Unfunded Mandates Reform Act (2
U.S.C. 1501 et seq.)
In accordance with the Unfunded
Mandates Reform Act (2 U.S.C. 1501 et
seq.), we make the following findings:
(1) This proposed rule will not
produce a Federal mandate. In general,
a Federal mandate is a provision in
legislation, statute, or regulation that
would impose an enforceable duty upon
State, local, or tribal governments, or the
private sector, and includes both
‘‘Federal intergovernmental mandates’’
and ‘‘Federal private sector mandates.’’
These terms are defined in 2 U.S.C.
658(5)–(7). ‘‘Federal intergovernmental
mandate’’ includes a regulation that
‘‘would impose an enforceable duty
upon State, local, or tribal governments’’
with two exceptions. It excludes ‘‘a
condition of Federal assistance.’’ It also
excludes ‘‘a duty arising from
participation in a voluntary Federal
program,’’ unless the regulation ‘‘relates
to a then-existing Federal program
under which $500,000,000 or more is
provided annually to State, local, and
tribal governments under entitlement
authority,’’ if the provision would
‘‘increase the stringency of conditions of
assistance’’ or ‘‘place caps upon, or
otherwise decrease, the Federal
Government’s responsibility to provide
funding,’’ and the State, local, or tribal
governments ‘‘lack authority’’ to adjust
accordingly. At the time of enactment,
these entitlement programs were:
Medicaid; Aid to Families with
Dependent Children work programs;
Child Nutrition; Food Stamps; Social
Services Block Grants; Vocational
Rehabilitation State Grants; Foster Care,
Adoption Assistance, and Independent
Living; Family Support Welfare
Services; and Child Support
Enforcement. ‘‘Federal private sector
mandate’’ includes a regulation that
‘‘would impose an enforceable duty
upon the private sector, except (i) a
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condition of Federal assistance or (ii) a
duty arising from participation in a
voluntary Federal program.’’
The designation of critical habitat
does not impose a legally binding duty
on non-Federal Government entities or
private parties. Under the Act, the only
regulatory effect is that Federal agencies
must ensure that their actions do not
destroy or adversely modify critical
habitat under section 7. While nonFederal entities that receive Federal
funding, assistance, or permits, or that
otherwise require approval or
authorization from a Federal agency for
an action, may be indirectly impacted
by the designation of critical habitat, the
legally binding duty to avoid
destruction or adverse modification of
critical habitat rests squarely on the
Federal agency. Furthermore, to the
extent that non-Federal entities are
indirectly impacted because they
receive Federal assistance or participate
in a voluntary Federal aid program, the
Unfunded Mandates Reform Act would
not apply, nor would critical habitat
shift the costs of the large entitlement
programs listed above onto State
governments.
(2) We lack the available economic
information to determine if a Small
Government Agency Plan is required.
Therefore, we defer this finding until
completion of the draft economic
analysis is prepared under section
4(b)(2) of the Act.
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Takings—Executive Order 12630
In accordance with Executive Order
12630 (Government Actions and
Interference with Constitutionally
Protected Private Property Rights), we
will analyze the potential takings
implications of designating critical
habitat for the Zuni bluehead sucker in
a takings implications assessment. The
draft economic analysis will provide the
foundation for us to use in preparing a
takings implication assessment. Critical
habitat designation does not affect
landowner actions that do not require
Federal funding or permits, nor does it
preclude development of habitat
conservation programs or issuance of
incidental take permits to permit actions
that do require Federal funding or
permits to go forward.
Federalism—Executive Order 13132
In accordance with Executive Order
13132 (Federalism), this proposed rule
does not have significant Federalism
effects. A Federalism assessment is not
required. In keeping with Department of
the Interior and Department of
Commerce policy, we requested
information from, and coordinated
development of, this proposed critical
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habitat designation with appropriate
State resource agencies in New Mexico
and Arizona. The designation of critical
habitat in areas currently occupied by
the Zuni bluehead sucker imposes no
additional restrictions to those currently
in place and, therefore, has little
incremental impact on State and local
governments and their activities. The
designation may have some benefit to
these governments because the areas
that contain the physical or biological
features essential to the conservation of
the species are more clearly defined,
and the elements of the features of the
habitat necessary to the conservation of
the species are specifically identified.
This information does not alter where
and what federally sponsored activities
may occur. However, it may assist local
governments in long-range planning
(rather than having them wait for caseby-case section 7 consultations to
occur).
Where State and local governments
require approval or authorization from a
Federal agency for actions that may
affect critical habitat, consultation
under section 7(a)(2) would be required.
While non-Federal entities that receive
Federal funding, assistance, or permits,
or that otherwise require approval or
authorization from a Federal agency for
an action, may be indirectly impacted
by the designation of critical habitat, the
legally binding duty to avoid
destruction or adverse modification of
critical habitat rests squarely on the
Federal agency.
Civil Justice Reform—Executive Order
12988
In accordance with Executive Order
12988 (Civil Justice Reform), the Office
of the Solicitor has determined that the
rule does not unduly burden the judicial
system and that it meets the
requirements of sections 3(a) and 3(b)(2)
of the Order. We are designating critical
habitat in accordance with the
provisions of the Act. To assist the
public in understanding the habitat
needs of the species, the rule identifies
the elements of physical or biological
features essential to the conservation of
the species. The designated areas of
critical habitat are presented on maps,
and the rule provides several options for
the interested public to obtain more
detailed location information, if desired.
Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.)
This rule does not contain any new
collections of information that require
approval by OMB under the Paperwork
Reduction Act of 1995 (44 U.S.C. 3501
et seq.). This rule will not impose
recordkeeping or reporting requirements
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on State or local governments,
individuals, businesses, or
organizations. An agency may not
conduct or sponsor, and a person is not
required to respond to, a collection of
information unless it displays a
currently valid OMB control number.
National Environmental Policy Act (42
U.S.C. 4321 et seq.)
It is our position that, outside the
jurisdiction of the U.S. Court of Appeals
for the Tenth Circuit, we do not need to
prepare environmental analyses
pursuant to NEPA in connection with
designating critical habitat under the
Endangered Species Act. We published
a notice outlining our reasons for this
determination in the Federal Register
on October 25, 1983 (48 FR 49244). This
position was upheld by the U.S. Court
of Appeals for the Ninth Circuit
(Douglas County v. Babbitt, 48 F.3d
1495 (9th Cir. 1995), cert. denied 516
U.S. 1042 (1996)). However, when the
range of the species includes States
within the Tenth Circuit, such as that of
the Zuni bluehead sucker, under the
Tenth Circuit ruling in Catron County
Board of Commissioners v. U.S. Fish
and Wildlife Service, 75 F.3d 1429 (10th
Cir. 1996), we will undertake a NEPA
analysis for critical habitat designation
and notify the public of the availability
of the draft environmental assessment
for this proposal when it is finished.
Government-to-Government
Relationship With Tribes
In accordance with the President’s
memorandum of April 29, 1994
(Government-to-Government Relations
with Native American Tribal
Governments; 59 FR 22951), Executive
Order 13175 (Consultation and
Coordination With Indian Tribal
Governments), and the Department of
the Interior’s manual at 512 DM 2, we
readily acknowledge our responsibility
to communicate meaningfully with
recognized Federal Tribes on a
government-to-government basis. In
accordance with Secretarial Order 3206
of June 5, 1997 (American Indian Tribal
Rights, Federal-Tribal Trust
Responsibilities, and the Endangered
Species Act), we readily acknowledge
our responsibilities to work directly
with tribes in developing programs for
healthy ecosystems, to acknowledge that
tribal lands are not subject to the same
controls as Federal public lands, to
remain sensitive to Indian culture, and
to make information available to tribes.
There are tribal lands in Arizona and
New Mexico included in this proposed
designation of critical habitat. Using the
criteria found in the Criteria Used To
Identify Critical Habitat section, we
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have determined that there are tribal
lands that are occupied by the Zuni
bluehead sucker that contain the
features essential for the conservation of
the species, as well as tribal lands
unoccupied by the species at the time of
listing that are essential for the
conservation of the Zuni bluehead
sucker. We have begun government-togovernment consultation with these
tribes throughout the public comment
period and during development of the
final designation of Zuni bluehead
sucker critical habitat. We will consider
these areas for exclusion from the final
critical habitat designation to the extent
consistent with the requirements of
section 4(b)(2) of the Act. The Navajo
Nation and Zuni Pueblo are the main
tribes affected by this proposed rule. We
sent notification letters in July 2012 to
each tribe describing the exclusion
process under section 4(b)(2) of the Act,
and we have engaged in conversations
with both tribes about the proposal to
the extent possible without disclosing
predecisional information. We
coordinated with the Navajo Nation in
May 2012 to coordinate surveys on
Navajo lands. Additionally, we are
working with Zuni Pueblo to develop a
management plan for their lands. We
will schedule meetings with these tribes
and any other interested tribes shortly
after publication of this proposed rule
so that we can give them as much time
as possible to comment.
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Clarity of the Rule
We are required by Executive Orders
12866 and 12988 and by the
Presidential Memorandum of June 1,
1998, to write all rules in plain
language. This means that each rule we
publish must:
(1) Be logically organized;
(2) Use the active voice to address
readers directly;
(3) Use clear language rather than
jargon;
(4) Be divided into short sections and
sentences; and
(5) Use lists and tables wherever
possible.
If you feel that we have not met these
requirements, send us comments by one
of the methods listed in the ADDRESSES
section. To better help us revise the
rule, your comments should be as
specific as possible. For example, you
should tell us the numbers of the
sections or paragraphs that are unclearly
written, which sections or sentences are
too long, the sections where you feel
lists or tables would be useful, etc.
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References Cited
A complete list of references cited in
this rulemaking is available on the
Internet at https://www.regulations.gov
and upon request from the New Mexico
Ecological Services Field Office (see FOR
FURTHER INFORMATION CONTACT).
Authors
The primary authors of this proposed
rule are the staff members of the New
Mexico Ecological Services Field Office.
List of Subjects in 50 CFR Part 17
Endangered and threatened species,
Exports, Imports, Reporting and
recordkeeping requirements,
Transportation.
Proposed Regulation Promulgation
Accordingly, we propose to amend
part 17, subchapter B of chapter I, title
50 of the Code of Federal Regulations,
as set forth below:
PART 17—[AMENDED]
1. The authority citation for part 17
continues to read as follows:
■
Authority: 16 U.S.C. 1361–1407; 1531–
1544; and 4201–4245, unless otherwise
noted.
2. In § 17.95, amend paragraph (e) by
adding an entry for ‘‘Zuni bluehead
sucker (Catostomus discobolus
yarrowi),’’ after the entry for ‘‘Warner
Sucker (Catostomus warnerensis)’’ to
read as follows:
■
§ 17.95
Critical habitat—fish and wildlife.
*
*
*
(e) Fishes.
*
*
*
*
*
*
*
Zuni bluehead sucker (Catostomus
discobolus yarrowi)
(1) Critical habitat units are depicted
for Apache County, Arizona, and Cibola,
McKinley, and San Juan Counties, New
Mexico, on the maps below.
(2) Within these areas, the primary
constituent elements of the physical or
biological features essential to the
conservation of the Zuni bluehead
sucker consist of three components:
(i) A riverine system with habitat to
support all life stages of Zuni bluehead
sucker, which includes:
(A) Dynamic flows that allow for
periodic changes in channel
morphology and adequate river
functions, such as channel reshaping
and delivery of coarse sediments.
(B) Stream courses with perennial
flows, or areas that may be periodically
dewatered but serve as connective
corridors between occupied or
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seasonally occupied habitat and through
which the species may move when the
habitat is wetted.
(C) Stream microhabitat types
including runs, riffles, and pools with
substrate ranging from gravel, cobble
and bedrock substrates with low or
moderate amounts of fine sediment and
substrate embeddedness.
(D) Streams with depths generally less
than 2 m (3.3 ft), and with slow to swift
flow velocities less than 35 cm/sec (1.1
ft/sec).
(E) Clear, cool water with low
turbidity and temperatures in the
general range of 9.0 to 28.0 °C (48.2 to
82.4 °F).
(F) No harmful levels of pollutants.
(G) Adequate riparian shading to
reduce water temperatures when
ambient temperatures are high and
provide protective cover from predators.
(ii) An abundant aquatic insect food
base consisting of fine particulate
organic material, filamentous algae,
midge larvae, caddisfly larvae, mayfly
larvae, flatworms, and small terrestrial
insects.
(iii) Areas devoid of nonnative aquatic
species or areas that are maintained to
kept nonnatives at a level that allows
the Zuni bluehead sucker to continue to
survive and reproduce.
(3) Critical habitat does not include
manmade structures (such as bridges,
docks, and aqueducts) and the land on
which they are located existing within
the legal boundaries on [DATE 30 DAYS
AFTER THE DATE OF PUBLICATION
OF THE FINAL RULE IN THE Federal
Register].
(4) Critical habitat map units. Data
layers defining map units were created
on a base of USGS digital ortho-photo
quarter-quadrangles, and critical habitat
units were then mapped using Universal
Transverse Mercator (UTM) Zone 15N
coordinates. The maps in this entry, as
modified by any accompanying
regulatory text, establish the boundaries
of the critical habitat designation. The
coordinates or plot points or both on
which each map is based are available
to the public at the Service’s Internet
site, (https://www.fws.gov/southwest/es/
NewMexico/), (https://
www.regulations.gov at Docket No.
FWS–R2–ES–2013–002 and at the New
Mexico Ecological Services Field Office.
You may obtain field office location
information by contacting one of the
Service regional offices, the addresses of
which are listed at 50 CFR part 22.
(5) Note: Index of critical habitat units
for the Zuni bluehead sucker follows:
BILLING CODE 4310–55–P
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(6) Unit 1: Zuni River Unit, McKinley
and Cibola Counties, New Mexico. Map
of Unit 1 follows:
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and San Juan Counties, New Mexico.
Map of Unit 2 follows:
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(7) Unit 2: Kinlichee Creek Unit,
Apache County, Arizona, and McKinley
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(8) Unit 3: San Juan River Unit,
Apache County, Arizona, and San Juan
County, New Mexico. Map of Unit 3 is
provided at paragraph (7) of this entry.
*
*
*
*
*
Dated: January 15, 2013.
Michael Bean,
Acting Principal Deputy Assistant Secretary
for Fish Wildlife and Parks.
[FR Doc. 2013–01302 Filed 1–24–13; 8:45 am]
BILLING CODE 4310–55–P
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–R2–ES–2012–0101;
4500030113]
RIN 1018–AY25
Endangered and Threatened Wildlife
and Plants; Proposed Endangered
Status for the Zuni Bluehead Sucker
AGENCY:
Fish and Wildlife Service,
Interior.
Proposed rule.
Executive Summary
ACTION:
We, the U.S. Fish and
Wildlife Service, propose to list the
Zuni bluehead sucker as an endangered
species under the Endangered Species
Act and propose to designate critical
habitat for the species. If we finalize this
rule as proposed, it would extend the
Act’s protections to this subspecies and
its critical habitat. The effect of these
regulations will be to conserve the Zuni
bluehead sucker and protect its habitat
under the Act.
DATES: We will accept comments
received or postmarked on or before
March 26, 2013. Comments submitted
electronically using the Federal
eRulemaking Portal (see ADDRESSES
section, below) must be received by
11:59 p.m. Eastern Time on the closing
date. We must receive requests for
public hearings, in writing, at the
address shown in FOR FURTHER
INFORMATION CONTACT by March 11,
2013.
SUMMARY:
You may submit comments
by one of the following methods:
(1) Electronically: Go to the Federal
eRulemaking Portal: https://
www.regulations.gov. In the Search box,
enter FWS–R2–ES–2012–0101, which is
the docket number for this rulemaking.
Then, in the Search panel on the left
side of the screen, under the Document
Type heading, click on the Proposed
Rules link to locate this document. You
may submit a comment by clicking on
‘‘Comment Now!’’
sroberts on DSK5SPTVN1PROD with
ADDRESSES:
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17:46 Jan 24, 2013
(2) By hard copy: Submit by U.S. mail
or hand-delivery to: Public Comments
Processing, Attn: FWS–R2–ES–2012–
0101; Division of Policy and Directives
Management; U.S. Fish and Wildlife
Service; 4401 N. Fairfax Drive, MS
2042–PDM; Arlington, VA 22203.
We request that you send comments
only by the methods described above.
We will post all comments on https://
www.regulations.gov. This generally
means that we will post any personal
information you provide us (see the
Public Comments section below for
more information).
FOR FURTHER INFORMATION CONTACT:
Wally ‘‘J’’ Murphy, Field Supervisor,
U.S. Fish and Wildlife Service, New
Mexico Ecological Services Field Office,
2105 Osuna NE., Albuquerque, NM
87113, by telephone 505–346–2525 or
by facsimile 505–346–2542. Persons
who use a telecommunications device
for the deaf (TDD) may call the Federal
Information Relay Service (FIRS) at
800–877–8339.
SUPPLEMENTARY INFORMATION:
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Why we need to publish a rule. Under
the Act, if a species is determined to be
an endangered or threatened species
throughout all or a significant portion of
its range, we are required to promptly
publish a proposal in the Federal
Register and make a determination on
our proposal within 1 year. Critical
habitat shall be designated, to the
maximum extent prudent and
determinable, for any species
determined to be an endangered or
threatened species under the Act.
Listing a species as an endangered or
threatened species and designations and
revisions of critical habitat can only be
completed by issuing a rule. Elsewhere
in today’s Federal Register, we propose
to designate critical habitat for the Zuni
bluehead sucker under the Act.
This rule consists of: (1) A proposed
rule to list the Zuni bluehead sucker
(Catostomus discobolus yarrowi) as an
endangered species; and (2) a proposed
rule for designation of critical habitat for
the Zuni bluehead sucker. The Zuni
bluehead sucker is a candidate species
for which we have on file sufficient
information on biological vulnerability
and threats to support preparation of a
listing proposal, but for which
development of a listing regulation has
been precluded by other higher priority
listing activities. This rule reassesses all
available information regarding status of
and threats to the Zuni bluehead sucker.
The basis for our action. Under the
Act, we can determine that a species is
an endangered or threatened species
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based on any of five factors: (A) The
present or threatened destruction,
modification, or curtailment of its
habitat or range; (B) Overutilization for
commercial, recreational, scientific, or
educational purposes; (C) Disease or
predation; (D) The inadequacy of
existing regulatory mechanisms; or (E)
Other natural or manmade factors
affecting its continued existence.
We have determined that the Zuni
bluehead sucker is threatened by
Factors A, C, D, and E.
We will seek peer review. We are
seeking comments from knowledgeable
individuals with scientific expertise to
review our analysis of the best available
science and application of that science
and to provide any additional scientific
information to improve this proposed
rule. Because we will consider all
comments and information received
during the comment period, our final
determinations may differ from this
proposal.
Information Requested
We intend that any final action
resulting from this proposed rule will be
based on the best scientific and
commercial data available and be as
accurate and as effective as possible.
Therefore, we request comments or
information from the public, other
concerned governmental agencies,
Native American tribes, the scientific
community, industry, or any other
interested parties concerning this
proposed rule. We particularly seek
comments concerning:
(1) The Zuni bluehead sucker’s
biology, range, and population trends,
including:
(a) Habitat requirements for feeding,
breeding, and sheltering;
(b) Genetics and taxonomy;
(c) Historical and current range
including distribution patterns;
(d) Historical and current population
levels, and current and projected trends;
and
(e) Past and ongoing conservation
measures for the species, its habitat or
both.
(2) The factors that are the basis for
making a listing determination for a
species under section 4(a) of the Act (16
U.S.C. 1531 et seq.), which are:
(a) The present or threatened
destruction, modification, or
curtailment of its habitat or range;
(b) Overutilization for commercial,
recreational, scientific, or educational
purposes;
(c) Disease or predation;
(d) The inadequacy of existing
regulatory mechanisms; or
(e) Other natural or manmade factors
affecting its continued existence.
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Agencies
[Federal Register Volume 78, Number 17 (Friday, January 25, 2013)]
[Proposed Rules]
[Pages 5351-5369]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-01302]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS-R2-ES-2013-0002; 4500030114]
RIN 1018-AZ23
Endangered and Threatened Wildlife and Plants; Proposed
Designation of Critical Habitat for the Zuni Bluehead Sucker
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service, propose to designate
critical habitat for the Zuni bluehead sucker. If we finalize this rule
as proposed, it would extend the Act's protections to this subspecies'
critical habitat. The effect of these regulations will be to protect
the Zuni bluehead sucker's habitat under the Act.
DATES: We will accept comments received or postmarked on or before
March 26, 2013. Comments submitted electronically using the Federal
eRulemaking Portal (see ADDRESSES section, below) must be received by
11:59 p.m. Eastern Time on the closing date. We must receive requests
for public hearings, in writing, at the address shown in FOR FURTHER
INFORMATION CONTACT by March 11, 2013.
ADDRESSES: You may submit comments by one of the following methods:
(1) Electronically: Go to the Federal eRulemaking Portal: https://www.regulations.gov. In the Search box, enter FWS-R2-ES-2013-0002,
which is the docket number for this rulemaking. Then, in the Search
panel on the left side of the screen, under the Document Type heading,
click on the Proposed Rules link to locate this document. You may
submit a comment by clicking on ``Comment Now!''
(2) By hard copy: Submit by U.S. mail or hand-delivery to: Public
Comments Processing, Attn: FWS-R2-ES-2013-0002; Division of Policy and
Directives Management; U.S. Fish and Wildlife Service; 4401 N. Fairfax
Drive, MS 2042-PDM; Arlington, VA 22203.
We request that you send comments only by the methods described
above. We will post all comments on https://www.regulations.gov. This
generally means that we will post any personal information you provide
us (see the Public Comments section below for more information).
The coordinates or plot points or both from which the critical
habitat maps are generated are included in the administrative record
for this rulemaking and are available at https://www.fws.gov/southwest/es/NewMexico/, https://www.regulations.gov at Docket No. FWS-R2-ES-2013-
0002, and at the New Mexico Ecological Services Field Office (see FOR
FURTHER INFORMATION CONTACT). Any additional tools or supporting
information that we may develop for this rulemaking will also be
available at the Fish and Wildlife Service Web site and Field Office
set out above, and may also be included in the preamble and/or at
www.regulations.gov.
FOR FURTHER INFORMATION CONTACT: Wally ``J'' Murphy, Field Supervisor,
U.S. Fish and Wildlife Service, New Mexico Ecological Services Field
Office, 2105 Osuna NE., Albuquerque, NM 87113, by telephone 505-346-
2525 or by facsimile 505-346-2542. Persons who use a telecommunications
device for the deaf (TDD) may call the Federal Information Relay
Service (FIRS) at 800-877-8339.
SUPPLEMENTARY INFORMATION:
Executive Summary
Why we need to publish a rule. Under the Act, once a species is
determined to be an endangered or threatened species throughout all or
a significant portion of its range, we are required to promptly publish
a proposal in the Federal Register and make a determination on our
proposal within 1 year. Additionally, critical habitat shall be
designated, to the maximum extent prudent and determinable, for any
species determined to be an endangered or threatened species under the
Act. Designations and revisions of critical habitat can only be
completed by issuing a rule. Elsewhere in today's Federal Register, we
propose to list the Zuni bluehead sucker as an endangered species under
the Act.
This rule consists of: A proposed rule for designation of critical
habitat for the Zuni bluehead sucker. The Zuni bluehead sucker has been
proposed for listing under the Act. This rule proposes designation of
critical habitat necessary for the conservation of the species.
The basis for our action. Under the Act, when a species is proposed
for listing, to the maximum extent prudent and determinable, we must
designate critical habitat for the species. The species has been
proposed for listing as endangered, and therefore, we also propose to
designate approximately 472 km (293 mi) of stream habitat as critical
habitat in Apache County, Arizona, and
[[Page 5352]]
Cibola, McKinley, and San Juan Counties, New Mexico, and on the Navajo
Indian Reservation.
We will seek peer review. We are seeking comments from
knowledgeable individuals with scientific expertise to review our
analysis of the best available science and application of that science
and to provide any additional scientific information to improve this
proposed rule. Because we will consider all comments and information
received during the comment period, our final determinations may differ
from this proposal.
Information Requested
We intend that any final action resulting from this proposed rule
will be based on the best scientific and commercial data available and
be as accurate and as effective as possible. Therefore, we request
comments or information from the public, other concerned governmental
agencies, Native American tribes, the scientific community, industry,
or any other interested parties concerning this proposed rule. We
particularly seek comments concerning:
(1) The reasons why we should or should not designate habitat as
``critical habitat'' under section 4 of the Act (16 U.S.C. 1531 et
seq.), including whether there are threats to the species from human
activity, the degree of which can be expected to increase due to the
designation, and whether that increase in threats outweighs the benefit
of designation such that the designation of critical habitat is not
prudent.
(2) Specific information on:
(a) The amount and distribution of the Zuni bluehead sucker and its
habitat;
(b) What may constitute ``physical or biological features essential
to the conservation of the species,'' within the geographical range
currently occupied by the species;
(c) Where these features are currently found;
(d) Whether any of these features may require special management
considerations or protection;
(e) What areas, that were occupied at the time of listing (or are
currently occupied) and that contain features essential to the
conservation of the species, should be included in the designation and
why; and
(f) What areas not occupied at the time of listing are essential
for the conservation of the species and why.
(3) Land use designations and current or planned activities in the
areas occupied by the species or proposed to be designated as critical
habitat, and possible impacts of these activities on this species and
proposed critical habitat.
(4) Information on the projected and reasonably likely impacts of
climate change on the Zuni bluehead sucker and proposed critical
habitat.
(5) Any foreseeable economic, national security, or other relevant
impacts that may result from designating any area that may be included
in the final designation. We are particularly interested in any impacts
on small entities, and the benefits of including or excluding areas
from the proposed designation that are subject to these impacts.
(6) Whether our approach to designating critical habitat could be
improved or modified in any way to provide for greater public
participation and understanding, or to assist us in accommodating
public concerns and comments.
(7) The likelihood of adverse social reactions to the designation
of critical habitat and how the consequences of such reactions, if
likely to occur, would relate to the conservation and regulatory
benefits of the proposed critical habitat designation.
Please include sufficient information with your submission (such as
scientific journal articles or other publications) to allow us to
verify any scientific or commercial information you include.
Please note that submissions merely stating support for or
opposition to the action under consideration without providing
supporting information, although noted, will not be considered in
making a determination, as section 4(b)(1)(A) of the Act directs that
determinations as to whether any species is a threatened or endangered
species must be made ``solely on the basis of the best scientific and
commercial data available.''
You may submit your comments and materials concerning this proposed
rule by one of the methods listed in the ADDRESSES section. We request
that you send comments only by the methods described in the ADDRESSES
section.
If you submit information via https://www.regulations.gov, your
entire submission--including any personal identifying information--will
be posted on the Web site. If your submission is made via a hardcopy
that includes personal identifying information, you may request at the
top of your document that we withhold this information from public
review. However, we cannot guarantee that we will be able to do so. We
will post all hardcopy submissions on https://www.regulations.gov.
Please include sufficient information with your comments to allow us to
verify any scientific or commercial information you include.
Comments and materials we receive, as well as supporting
documentation we used in preparing this proposed rule, will be
available for public inspection on https://www.regulations.gov, or by
appointment, during normal business hours, at the U.S. Fish and
Wildlife Service, New Mexico Ecological Services Field Office (see FOR
FURTHER INFORMATION CONTACT).
Previous Federal Actions
All previous Federal actions are described in the proposal to list
the Zuni bluehead sucker as an endangered species under the Act
published elsewhere in today's Federal Register.
Critical Habitat Designation for the Zuni Bluehead Sucker
Background
Critical habitat is defined in section 3 of the Act as:
(1) The specific areas within the geographical area occupied by the
species, at the time it is listed in accordance with the Act, on which
are found those physical or biological features:
(a) Essential to the conservation of the species, and
(b) Which may require special management considerations or
protection; and
(2) Specific areas outside the geographical area occupied by the
species at the time it is listed, upon a determination that such areas
are essential for the conservation of the species.
Conservation, as defined under section 3 of the Act, means to use
and the use of all methods and procedures that are necessary to bring
an endangered or threatened species to the point at which the measures
provided pursuant to the Act are no longer necessary. Such methods and
procedures include, but are not limited to, all activities associated
with scientific resources management such as research, census, law
enforcement, habitat acquisition and maintenance, propagation, live
trapping, and transplantation, and, in the extraordinary case where
population pressures within a given ecosystem cannot be otherwise
relieved, may include regulated taking.
Critical habitat receives protection under section 7 of the Act
through the requirement that Federal agencies ensure, in consultation
with the Service, that any action they authorize, fund, or carry out is
not likely to result in the destruction or adverse modification of
[[Page 5353]]
critical habitat. The designation of critical habitat does not affect
land ownership or establish a refuge, wilderness, reserve, preserve, or
other conservation area. Such designation does not allow the government
or public to access private lands. Such designation does not require
implementation of restoration, recovery, or enhancement measures by
non-Federal landowners. Where a landowner requests Federal agency
funding or authorization for an action that may affect a listed species
or critical habitat, the consultation requirements of section 7(a)(2)
of the Act would apply, but even in the event of a destruction or
adverse modification finding, the obligation of the Federal action
agency and the landowner is not to restore or recover the species, but
to implement reasonable and prudent alternatives to avoid destruction
or adverse modification of critical habitat.
Under the first prong of the Act's definition of critical habitat,
areas within the geographical area occupied by the species at the time
it was listed are included in a critical habitat designation if they
contain physical or biological features (1) essential to the
conservation of the species, and (2) which may require special
management considerations or protection. For these areas, critical
habitat designations identify, to the extent known using the best
scientific and commercial data available, those physical or biological
features essential to the conservation of the species (such as space,
food, cover, and protected habitat). In identifying those physical or
biological features within an area, we focus on the principal
biological or physical constituent elements (primary constituent
elements such as roost sites, nesting grounds, seasonal wetlands, water
quality, tide, soil type) that are essential to the conservation of the
species. Primary constituent elements are those specific elements of
the physical or biological features that provide for a species' life-
history processes and are essential to the conservation of the species.
Under the second prong of the Act's definition of critical habitat,
we can designate critical habitat in areas outside the geographic area
occupied by the species at the time it is listed, upon a determination
that such areas are essential for the conservation of the species. For
example, an area currently occupied by the species but that was not
occupied at the time of listing may be essential to the conservation of
the species and may be included in the critical habitat designation. We
designate critical habitat in areas outside the geographic area
occupied by a species only when a designation limited to its range
would be inadequate to ensure the conservation of the species.
Section 4 of the Act requires that we designate critical habitat on
the basis of the best scientific data available. Further, our Policy on
Information Standards Under the Endangered Species Act (published in
the Federal Register on July 1, 1994 (59 FR 34271)), the Information
Quality Act (section 515 of the Treasury and General Government
Appropriations Act for Fiscal Year 2001 (Pub. L. 106-554; H.R. 5658)),
and our associated Information Quality Guidelines, provide criteria,
establish procedures, and provide guidance to ensure that our decisions
are based on the best scientific data available. They require our
biologists, to the extent consistent with the Act and with the use of
the best scientific data available, to use primary and original sources
of information as the basis for recommendations to designate critical
habitat.
When we are determining which areas should be designated as
critical habitat, our primary source of information is generally the
information developed during the listing process for the species.
Additional information sources may include the recovery plan for the
species, articles in peer-reviewed journals, conservation plans
developed by States and counties, scientific status surveys and
studies, biological assessments, other unpublished materials, or
experts' opinions or personal knowledge.
Habitat is dynamic, and species may move from one area to another
over time. Climate change will be a particular challenge for
biodiversity because the interaction of additional stressors associated
with climate change and current stressors may push species beyond their
ability to survive (Lovejoy 2005, pp. 325-326). The synergistic
implications of climate change and habitat fragmentation are the most
threatening facet of climate change for biodiversity (Hannah and
Lovejoy 2005, p. 4). Current climate change predictions for terrestrial
areas in the Northern Hemisphere indicate warmer air temperatures, more
intense precipitation events, and increased summer continental drying
(Field et al. 1999, pp. 1-3; Hayhoe et al. 2004, p. 12422; Cayan et al.
2005, p. 6; Intergovernmental Panel on Climate Change (IPCC) 2007, p.
1181). Climate change may lead to increased frequency and duration of
severe storms and droughts (Golladay et al. 2004, p. 504; McLaughlin et
al. 2002, p. 6074; Cook et al. 2004, p. 1015).
We recognize that critical habitat designated at a particular point
in time may not include all of the habitat areas that we may later
determine are necessary for the recovery of the species. For these
reasons, a critical habitat designation does not signal that habitat
outside the designated area is unimportant or may not be needed for
recovery of the species. Areas that are important to the conservation
of the species, both inside and outside the critical habitat
designation, will continue to be subject to: (1) Conservation actions
implemented under section 7(a)(1) of the Act, (2) regulatory
protections afforded by the requirement in section 7(a)(2) of the Act
for Federal agencies to ensure their actions are not likely to
jeopardize the continued existence of any endangered or threatened
species, and (3) section 9 of the Act's prohibitions on taking any
individual of the species, including taking caused by actions that
affect habitat. Federally funded or permitted projects affecting listed
species outside their designated critical habitat areas may still
result in jeopardy findings in some cases. These protections and
conservation tools will continue to contribute to recovery of this
species. Similarly, critical habitat designations made on the basis of
the best available information at the time of designation will not
control the direction and substance of future recovery plans, habitat
conservation plans (HCPs), or other species conservation planning
efforts if new information available at the time of these planning
efforts calls for a different outcome.
Prudency Determination
Section 4(a)(3) of the Act, as amended, and implementing
regulations (50 CFR 424.12), require that, to the maximum extent
prudent and determinable, the Secretary designate critical habitat at
the time the species is determined to be an endangered or threatened
species. Our regulations (50 CFR 424.12(a)(1)) state that the
designation of critical habitat is not prudent when one or both of the
following situations exist: (1) The species is threatened by taking or
other human activity, and identification of critical habitat can be
expected to increase the degree of threat to the species, or (2) such
designation of critical habitat would not be beneficial to the species.
There is currently no immediate threat of take attributed to
collection or vandalism under Factor B for this species, and
identification and mapping
[[Page 5354]]
of critical habitat is not expected to initiate any such threat. In the
absence of finding that the designation of critical habitat would
increase threats to a species, if there are any benefits to a critical
habitat designation, then a prudent finding is warranted. Here, the
potential benefits of designation include: (1) Triggering consultation
under section 7 of the Act, in new areas for actions in which there may
be a Federal nexus where it would not otherwise occur because, for
example, it is or has become unoccupied or the occupancy is in
question; (2) focusing conservation activities on the most essential
features and areas; (3) providing educational benefits to State or
county governments or private entities; and (4) preventing people from
causing inadvertent harm to the species. Therefore, because we have
determined that the designation of critical habitat will not likely
increase the degree of threat to the species and may provide some
measure of benefit, we find that designation of critical habitat is
prudent for the Zuni bluehead sucker.
Critical Habitat Determinability
Having determined that designation is prudent, under section
4(a)(3) of the Act, we must find whether critical habitat for the Zuni
bluehead sucker is determinable. Our regulations at 50 CFR 424.12(a)(2)
state that critical habitat is not determinable when one or both of the
following situations exist:
(i) Information sufficient to perform required analyses of the
impacts of the designation is lacking, or
(ii) The biological needs of the species are not sufficiently well
known to permit identification of an area as critical habitat.
When critical habitat is not determinable, the Act allows the
Service an additional year to publish a critical habitat designation
(16 U.S.C. 1533(b)(6)(C)(ii)).
We reviewed the available information pertaining to the biological
needs of the species and habitat characteristics where the species is
located. This and other information represent the best scientific data
available and led us to conclude that the designation of critical
habitat is determinable for the Zuni bluehead sucker.
Physical or Biological Features
In accordance with section 3(5)(A)(i) and 4(b)(1)(A) of the Act and
regulations at 50 CFR 424.12, in determining which areas within the
geographic area occupied by the species at the time of listing to
designate as critical habitat, we consider the physical or biological
features that are essential to the conservation of the species and
which may require special management considerations or protection.
These include, but are not limited to:
(1) Space for individual and population growth and for normal
behavior;
(2) Food, water, air, light, minerals, or other nutritional or
physiological requirements;
(3) Cover or shelter;
(4) Sites for breeding, reproduction, or rearing (or development)
of offspring; and
(5) Habitats that are protected from disturbance or are
representative of the historical, geographic, and ecological
distributions of a species.
We derive the specific physical or biological features required for
the Zuni bluehead sucker from studies of this species' habitat,
ecology, and life history as described below. Habitat needs for
specific life stages for Zuni bluehead sucker have not been described;
therefore, when necessary we will rely on information available for the
bluehead sucker, which is closely related to the Zuni bluehead sucker.
Space for Individual and Population Growth and for Normal Behavior
Zuni bluehead sucker occur in stream habitats with abundant shade
from overhanging vegetation and boulders, in pools, runs, and riffles
with water velocities ranging from 0 to 0.35 m/sec (1.15 ft/sec) or
less and ranging in depth from 0.2-2.0 m (7.9-78.7 in) (Hanson 1980,
pp. 34, 42; Propst and Hobbes 1996, pp. 13, 16; Gilbert and Carmen
2011, pp. 8-10). Shade provided by the overhanging vegetation curtails
water temperature fluctuations in small, headwater streams, such as
those occupied by Zuni bluehead sucker (Whitledge et al. 2006, p.
1461). Substrate in Zuni bluehead sucker habitat ranges from silt and
pebbles to cobbles, boulders, and bedrock (Hanson 1980, pp. 34, 42;
Propst and Hobbes 1996, pp. 13, 16; Gilbert and Carmen 2011, pp. 8-10;
NMDGF 2012). Clean substrate, such as gravel and coarse sand, free of
silt, is necessary for spawning and egg development (Maddux and Kepner
1988, p. 364). Excessive levels of silt can inhibit egg and juvenile
fish development through the clogging of the small spaces between
substrate particles, which prevents the free flow of oxygenated water.
Additionally, siltation can reduce the suitability of the habitat for
prey organisms. Juvenile bluehead sucker have been found nearshore in
slower and shallower habitats, then moving out into deeper water and
faster flowing habitat as they age (Childs et al. 1998, p. 624).
Water temperatures in occupied habitats in New Mexico have ranged
from 9.9 to 25.2 degrees Celsius ([deg]C) (49.8 to 77.3 degrees
Fahrenheit ([deg]F)) during survey efforts (Propst et al. 2001, p. 163;
Gilbert and Carmen 2011, pp. 8-10). Year-round data loggers have
recorded temperatures as low as -3.2[deg]C (24.3 [deg]F) and as high as
24.1[deg]C (75.3 [deg]F) (Gilbert and Carmen 2011, pp. 8-10).
Therefore, based on the information above, we identify the
following habitat parameters as the physical or biological features for
the Zuni bluehead sucker:
A variety of stream habitats, including riffles, runs, and
pools, with appropriate flows and substrates, with low to moderate
amounts of fine sediment and substrate embeddedness, as maintained by
natural, unregulated flow that allows for periodic flooding or, if
flows are modified or regulated, flow patterns that allow the river to
mimic natural functions, such as flows capable of transporting
sediment.
Food, Water, Air, Light, Minerals, or Other Nutritional or
Physiological Requirements
Food. The Zuni bluehead sucker is a benthic forager (eats food from
the stream bottom) that scrapes algae, insects, and other organic and
inorganic material from the surface of rocks (NMDGF 2004, p. 8).
Stomach content analysis of Zuni bluehead suckers revealed small
particulate organic matter, including detritus (nonliving organic
material), algae, small midge (two-winged fly) larvae, caddisfly
larvae, mayfly larvae, flatworms, and the occasional small terrestrial
insects (Smith and Koehn 1979, p. 38). In addition, Smith and Koehn
(1979, p. 38) also found fish scales, snails, and insect eggs in Zuni
bluehead sucker stomachs.
The primary source of food for Zuni bluehead sucker is periphytic
algae (algae attached to rocks), which occurs mainly on cobble,
boulder, and bedrock substrates with clean flowing water. Diet
preferences have been described for adults, but not for the remaining
life stages of Zuni bluehead sucker. Larval bluehead suckers (<25 mm
(approx.1 in) total length) feed on diatoms (a type of algae),
zooplankton (small floating or swimming organisms that drift with water
currents), and dipteran larvae (true fly larvae) in stream areas with
low velocity or in backwater habitats (Muth and Snyder 1995, p. 100).
Juvenile and adult bluehead sucker are reported primarily to eat a
variety of inorganic material, organic material, and bottom-dwelling
insects and other small organisms (Childs et al. 1998, p. 625;
[[Page 5355]]
Osmundson 1999, p. 28; Brooks et al. 2000, pp. 66-69).
Aquatic invertebrates are another important component of the Zuni
bluehead sucker diet. These aquatic invertebrates have specific habitat
requirements of their own. Both caddisflies and mayflies occur
primarily in a wide variety of standing and running-water habitats with
the greatest diversity being found in rocky-bottom streams with an
abundance of oxygen (Merritt and Cummins 1996, pp. 126, 309).
Caddisflies and mayflies feed on a variety of detritus, algae, diatoms,
and macrophytes (aquatic plants) (Merritt and Cummins 1996, pp. 126,
309). Habitat that consists of rocky bottoms with periphytic algal
growth is not only important to sustain aquatic invertebrate
populations (a Zuni bluehead sucker food source), but also serves as a
primary food resource of the Zuni bluehead sucker.
Water. As a purely aquatic species, Zuni bluehead sucker is
entirely dependent on stream habitat for all stages of their life
cycle. Therefore, perennial flows are an essential feature with
appropriate seasonal flows to maintain habitat conditions that remove
excess sediments. Areas with intermittent flows may serve as connective
corridors between occupied or seasonally occupied habitat through which
the species may move when the habitat is wetted.
There is very little information on water quality requirements for
Zuni bluehead sucker. However, excessive sedimentation is the primary
threat to water quality for the Zuni bluehead sucker (as discussed
above), primarily due to its effects on reproduction and food
resources. Turbidity (sediment suspended in the water column) can
inhibit algae production through reducing sunlight penetration into the
water.
Therefore, based on the information above, we identify the
following prey base and water quality characteristics as physical or
biological features for the Zuni bluehead sucker:
An abundant source of algae production and an aquatic
insect food base consisting of caddisflies, mayflies, midges, and
various terrestrial insects;
Streams with no harmful levels of pollutants;
Areas devoid of sediment deposition;
Perennial flows, or interrupted stream courses that are
periodically dewatered but that serve as connective corridors between
occupied or seasonally occupied habitat and through which the species
may move when the habitat is wetted;
Dynamic flows that allow for periodic changes in channel
morphology.
Cover or Shelter
Cover from predation may be in the form of deep water or physical
structure. Very little is known about habitat parameters specifically
relating to cover for Zuni bluehead sucker. However, during surveys,
Zuni bluehead sucker have been found in shaded pools and near boulder
outcrops, which may be used for cover (Kitcheyan 2012, pers. comm.).
Additionally, mature bluehead sucker are found in deeper water than
larvae and in habitats with less woody cover than younger life stages,
which are more vulnerable to predation (Childs et al. 1998, p. 624).
Sites for Breeding, Reproduction, or Rearing (or Development) of
Offspring
Zuni bluehead sucker spawn from early April to early June when
water temperatures are 6 to 15 [deg]C (43 to 59 [deg]F), peaking around
10 [deg]C (50 [deg]F) (Propst 1999, p. 50; Propst et al. 2001, p. 164).
Zuni bluehead sucker may have two spawning periods, with the majority
of the spawning effort expended early in the season (Propst et al.
2001, p. 158). Females in spawning condition have been found over
gravel beds (Sublette et al. 1990, p. 210; Propst et al. 2001, p. 158),
Clean substrates free of excessive sedimentation are essential for
successful breeding (see Habitat and Life History section of our
proposed listing rule published elsewhere in today's Federal Register).
Periodic flooding removes excess silt and fine sand from the stream
bottom, breaks up embedded bottom materials, and rearranges sediments
in ways that promote algae production and create suitable habitats with
silt-free substrates.
Therefore, based on the information above, we identify the
following parameters for breeding, reproduction, or development of
offspring as physical or biological features for the Zuni bluehead
sucker:
Gravel and cobble substrates;
Pool habitat;
Slower currents along stream margins with appropriate
stream velocities for larvae;
Instream flow velocities that are less than 35 cm/sec (1.1
ft/sec); and
Dynamic flows that allow for periodic changes in channel
morphology.
Habitats Protected From Disturbance or Representative of the
Historical, Geographic, and Ecological Distributions of the Species
The Zuni bluehead sucker has a restricted geographic distribution.
Endemic species (species that are exclusively native to a particular
location) whose populations exhibit a high degree of isolation are
extremely susceptible to extinction from both random and nonrandom
catastrophic natural or human-caused events. Therefore, it is essential
to maintain both springs and stream systems upon which the Zuni
bluehead sucker depends. This means protection from disturbance caused
by exposure to land management actions (logging, cattle grazing, and
road construction), water contamination, water depletion, beaver dams,
or nonnative species. The Zuni bluehead sucker must, at a minimum,
sustain its current distribution for the species to continue to
persist., Introduced species are a serious threat to native aquatic
species (Miller 1961, pp. 365, 397-398; Lachner et al. 1970, p. 21; Ono
et al. 1983, pp. 90-91; Carlson and Muth 1989, pp. 222, 234; Fuller et
al. 1999, p. 1; Propst et al. 2008, pp. 1246-1251; Pilger et al. 2010,
pp. 300, 311-312; see both Factor C: Disease and Predation, and Factor
E: Other Natural or Manmade Factors Affecting Its Continued Existence
sections of our proposed listing rule published elsewhere in today's
Federal Register). Because the distribution of the Zuni bluehead sucker
is so isolated and its habitat so restricted, introduction of certain
nonnative species into its habitat could be devastating. Potentially
harmful nonnative species include green sunfish, northern crayfish,
fathead minnow, and other nonnative fish-eating fishes.
Zuni bluehead sucker typically inhabit small desert stream systems
including isolated headwater springs, small headwater springs, and
mainstem river habitats (Gilbert and Carman 2011, p. 2) with clean,
hard substrate, flowing water, and abundant riparian vegetation.
Degraded habitat consists of silt-laden substrates, high turbidity, and
deep, stagnant water (Gilbert and Carman 2011, p. 6). Ponds formed by
beaver dams and impoundments as well as pools formed during river
intermittency create such degraded habitats. Therefore, based on the
information above, we identify the necessary physical or biological
features for the Zuni bluehead sucker:
Nondegraded habitat devoid of nonnative aquatic species,
or habitat in
[[Page 5356]]
which nonnative aquatic species are at levels that allow persistence of
Zuni bluehead sucker.
Primary Constituent Elements for the Zuni Bluehead Sucker
Under the Act and its implementing regulations, we are required to
identify the physical or biological features essential to the
conservation of the Zuni bluehead sucker in areas occupied at the time
of listing, focusing on the features' primary constituent elements. We
consider primary constituent elements to be the elements of physical or
biological features that provide for a species' life-history processes
and are essential to the conservation of the species.
Based on our current knowledge of the physical or biological
features and habitat characteristics required to sustain the species'
life-history processes, we determine that the primary constituent
elements specific to the Zuni bluehead sucker are:
(1) A riverine system with habitat to support all life stages of
Zuni bluehead sucker (egg, larval, juvenile, and adult), which
includes:
a. Dynamic flows that allow for periodic changes in channel
morphology and adequate river functions, such as channel reshaping and
delivery of coarse sediments.
b. Stream courses with perennial flows, or areas that may be
periodically dewatered but serve as connective corridors between
occupied or seasonally occupied habitat and through which the species
may move when the habitat is wetted;
c. Stream microhabitat types including runs, riffles, and pools
with substrate ranging from gravel, cobble, and bedrock substrates with
low or moderate amounts of fine sediment and substrate embeddedness;
and
d. Streams with depths generally less than 2 m (3.3 ft), and with
slow to swift flow velocities less than 35 cm/sec (1.1 ft/sec);
e. Clear, cool water with low turbidity and temperatures in the
general range of 9.0 to 28.0 [deg]C (48.2 to 82.4 [deg]F).
f. No harmful levels of pollutants;
g. Adequate riparian shading to reduce water temperatures when
ambient temperatures are high and provide protective cover from
predators; and
(2) An abundant aquatic insect food base consisting of fine
particulate organic material, filamentous algae, midge larvae,
caddisfly larvae, mayfly larvae, flatworms, and small terrestrial
insects.
(3) Areas devoid of nonnative aquatic species or areas that are
maintained to kept nonnatives at a level that allows the Zuni bluehead
sucker to continue to survive and reproduce.
Special Management Considerations or Protection
When designating critical habitat, we assess whether the specific
areas within the geographic area occupied by the species at the time of
listing contain features which are essential to the conservation of the
species and which may require special management considerations or
protection. We believe each area included in these designations
requires special management and protections as described in our unit
descriptions.
We need to consider special management considerations or protection
for the features essential to the conservation of the species within
each critical habitat area. The special management considerations or
protections will depend on the threats to the essential features in
that critical habitat area. For example, threats requiring special
management considerations or protection include the continued spread of
nonnative fish species into Zuni bluehead sucker habitat or increasing
number of beavers that reduce habitat quality and foster expansion of
nonnative fish and crayfish. Other threats requiring special management
considerations or protection include the threat of wildfire and
excessive ash and sediment following fire. Improper livestock grazing
can be a threat to the remaining populations of Zuni bluehead sucker
through trampling of habitat and increasing sedimentation. Inadequate
water quantity resulting from drought and water withdrawals affect all
life stages of Zuni bluehead sucker. Additionally, the construction of
impoundments and water diversions can cause an increase in water depth
behind the structure and a reduction or elimination of stream habitat
below.
We have included below in our description of each of the critical
habitat areas for the Zuni bluehead sucker a discussion of the threats
occurring in that area requiring special management considerations or
protection.
Criteria Used To Identify Critical Habitat
As required by Section 4(b)(2) of the Act, we use the best
scientific data available to designate critical habitat. We review
available information pertaining to the habitat requirements of the
species. In accordance with the Act and its implementing regulation at
50 CFR 424.12(e), we consider whether designating additional areas--
outside those currently occupied as well as those occupied at the time
of listing--are necessary to ensure the conservation of the species. We
are proposing to designate critical habitat in areas within the
geographic area occupied by the species at the time of listing, as
described above in the proposed rule to list the Zuni bluehead sucker,
and that contain sufficient elements of physical or biological features
to support life-history processes essential for the conservation of the
species. We are also proposing to designate specific areas outside the
geographic area occupied by the species at the time of listing because
such areas are essential for the conservation of the species.
Sources of data for this species include multiple databases
maintained by universities and State agencies for Arizona and New
Mexico, existing State recovery plans, endangered species reports, and
numerous survey reports on streams throughout the species' range
(Sanchez 1975, pp. 1, 4; Propst et al. 1986, pp. 49-51; NMDGF 2003, pp.
6-10; Sponholtz 2003, pp. 18-22; NMDGF 2004, pp. 1-40; Clarkson and
Marsh 2006, pp. 1-2; David 2006, pp. 1-40; NMDGF 2007, pp. 1-27;
Douglas et al. 2009, p. 67; Service 2010, pp. 1-2; NMDGF 2012; Navajo
Nation Heritage Program 2012, pp. 1-20). We have also reviewed
available information that pertains to the habitat requirements of this
species. Sources of information on habitat requirements include
existing State recovery plans, endangered species reports, studies
conducted at occupied sites and published in peer-reviewed articles,
agency reports, and data collected during monitoring efforts (Propst et
al. 2001, pp. 159-161; NMDGF 2003, pp. 1-14; NMDGF 2004, pp. 4-7).
The current distribution of the Zuni bluehead sucker is much
reduced from its historical distribution. We anticipate that recovery
will require continued protection of existing populations and habitat,
as well as establishing populations in additional streams that more
closely approximate its historic distribution in order to ensure there
are adequate numbers of fish in stable populations and that these
populations occur over a wide geographic area. This will help to ensure
that catastrophic events, such as wildfire, cannot simultaneously
affect all known populations.
Areas Occupied at the Time of Listing
The proposed critical habitat designation does not include all
streams known to have been occupied by the species historically;
instead, it focuses on occupied streams within the
[[Page 5357]]
historical range that have retained the necessary PCEs that will allow
for the maintenance and expansion of existing populations. The
following streams meet the definition of areas occupied by the species
at the time of listing: Agua Remora, Rio Nutria, Tampico Spring,
Tampico Draw, Kinlichee Creek, Black Soil Wash, Scattered Willow Wash,
Coyote Wash, Crystal Creek, Sonsela Creek, Tsaile Creek, Wheatfields
Creek, and Whiskey Creek. There are no developed areas within the
proposed designation except for barriers constructed on streams or road
crossings of streams, which do not remove the suitability of these
areas for this species.
Areas Outside of the Geographic Range at the Time of Listing
The Zuni River, Rio Pescado, Cebolla Creek, Red Clay Wash,
Palisades Creek, and Little Whiskey Creek are within the historical
range of the Zuni bluehead sucker but are not within the geographic
range currently occupied by the species; the Zuni River and Rio Pescado
experience a high degree of river intermittency, and the Zuni bluehead
sucker has not been seen in Cebolla Creek, Red Clay Wash, and Little
Whiskey Creek in over 30 years, and it has not been observed in the
Zuni River or Rio Pescado in approximately 20 years. We consider these
sites to be extirpated. For areas not occupied by the species at the
time of listing, we must demonstrate that these areas are essential to
the conservation of the species in order to include them in our
critical habitat designation. To determine if these areas are essential
for the conservation of the Zuni bluehead sucker, we considered: (1)
The importance of the site to the overall status of the species to
prevent extinction and contribute to future recovery of the Zuni
bluehead sucker; (2) whether the area could be restored to contain the
necessary habitat to support the Zuni bluehead sucker; (3) does the
site provide connectivity between occupied sites for genetic exchange:
and (4) whether a population of the species could be reestablished in
the area.
Of the unoccupied streams, the Zuni River, Rio Pescado, and
Palisades Creek exhibit varying degrees of intermittency; the Zuni
River and Rio Pescado are generally only continuous after heavy flows
in the spring (NMDGF 2004, p. 13; New Mexico Environment Department
(NMED) 2004, p. 1), and Palisades Creek has been noted as dry during
recent visits (Hobbes 2001, pp. 25-26; Carman 2004, p. 9). However,
when the Zuni River, Rio Pescado, and Cebolla Creek do exhibit flow and
if suitable habitat were restored, they could allow for important
population expansion in this watershed and they are therefore essential
for the conservation of the Zuni bluehead sucker. On the other hand,
Palisades Creek is a tributary to Whiskey Creek that, when wetted,
likely does not provide much benefit to the species. Because this
formerly occupied site has been so severely impacted and, as a small
tributary, it does not connect occupied sites, it is unlikely to
contribute to the recovery of the species and is not considered
essential to the conservation of the species. Therefore, it is not
included in the proposed designation of critical habitat.
In summary, for areas within the geographic area occupied by the
species at the time of listing, we delineated critical habitat unit
boundaries using the following criterion:
(1) Evaluate habitat suitability of stream segments within the
geographic area occupied at the time of listing, and retain those
segments that contain some or all of the PCEs to support life-history
functions essential for conservation of the species.
For areas outside the geographic area occupied by the species at
the time of listing, we delineated critical habitat unit boundaries
using the following steps:
(2) Evaluate stream segments not known to have been occupied at
listing but that are within the historical range of the species
(outside of the geographic area occupied by the species) to determine
if they are essential to the survival and recovery of the species.
Essential areas are those that:
(a) Serve as an extension of habitat within the geographic area of
an occupied unit;
(b) Expand the geographic distribution within areas not occupied at
the time of listing across the historical range of the species; and
(c) Are connected to other occupied areas, which will enhance
genetic exchange between populations.
We conclude that the areas proposed for critical habitat provide
for the conservation of the Zuni bluehead sucker because they include
habitat for all extant populations and include habitat for connectivity
and dispersal opportunities within units. Such opportunities for
dispersal assist in maintaining the population structure and
distribution of the species. The current amount of habitat that is
occupied is not sufficient for the recovery of the species; therefore,
we included unoccupied habitat in this proposed critical habitat
designation.
As a final step, we evaluated those occupied stream segments
retained through step 1 of the above analysis and refined the starting
and ending points by evaluating the presence or absence of appropriate
PCEs. We selected upstream and downstream cutoff points to omit areas
that are highly degraded and are not likely restorable. For example,
permanently dewatered areas, or areas in which there was a change to
unsuitable parameters (e.g., water quality, bedrock substrate) were
used to mark the start or endpoint of a stream segment proposed for
designation. Critical habitat stream segments were then mapped using
ArcMap version 10 (Environmental Systems Research Institute, Inc.), a
Geographic Information Systems program.
The areas proposed for designation as critical habitat provide
sufficient stream and spring habitat for breeding, nonbreeding, and
dispersing adult Zuni bluehead sucker, as well as for the habitat needs
for juvenile and larval stages of this fish. In general, the PCEs of
critical habitat are contained within the riverine ecosystem formed by
the wetted channel and the adjacent floodplains within 91.4 lateral m
(300 lateral ft) on either side of bankfull stage, except where bounded
by canyon walls. Areas within the lateral extent also contribute to the
PCEs, including water quality and intermittent areas through which fish
may move when wetted. Zuni bluehead sucker use the riverine ecosystem
for feeding, breeding, and sheltering while breeding and migrating.
When determining proposed critical habitat boundaries, we made
every effort to avoid including developed areas such as lands covered
by bridges, docks, aqueducts, and other structures because such lands
lack physical or biological features for the Zuni bluehead sucker. The
scale of the maps we prepared under the parameters for publication
within the Code of Federal Regulations may not reflect the exclusion of
such developed lands. Any such lands inadvertently left inside critical
habitat boundaries shown on the maps of this proposed rule have been
excluded by text in the proposed rule and are not proposed for
designation as critical habitat. Therefore, if the critical habitat is
finalized as proposed, a Federal action involving these lands would not
trigger section 7 consultation with respect to critical habitat and the
requirement of no adverse modification unless the specific action would
affect the physical or biological features in the adjacent critical
habitat.
We are proposing for designation of critical habitat lands that we
have determined are occupied at the time of listing and contain
sufficient elements
[[Page 5358]]
of physical or biological features to support life-history processes
essential for the conservation of the species, and lands outside of the
geographic area occupied at the time of listing that we have determined
are essential for the conservation of the Zuni bluehead sucker.
Segments were proposed for designation based on sufficient elements
of physical or biological features being present to support the Zuni
bluehead sucker life-history processes. Some segments contained all of
the identified elements of physical or biological features and
supported multiple life-history processes. Some segments contained only
some elements of the physical or biological features necessary to
support the Zuni bluehead sucker's particular use of that habitat.
The critical habitat designation is defined by the map or maps, as
modified by any accompanying regulatory text, presented at the end of
this document in the rule portion. We include more detailed information
on the boundaries of the critical habitat designation in the preamble
of this document. We will make the coordinates or plot points or both
on which each map is based available to the public on https://www.regulations.gov at Docket No. FWS-R2-ES-2012-0101, on our Internet
sites https://www.fws.gov/southwest/es/NewMexico/, and at the field
office responsible for the designation (see FOR FURTHER INFORMATION
CONTACT above).
Proposed Critical Habitat Designation
We are proposing to designate approximately 472 km (293 mi) in
three units as critical habitat for the Zuni bluehead sucker. The
critical habitat areas we describe below constitute our current best
assessment of areas that meet the definition of critical habitat for
Zuni bluehead sucker. The three areas we propose as critical habitat
are: (1) Zuni River Unit; (2) Kinlichee Creek Unit; and (3) San Juan
River Unit. Table 1 shows the occupancy of the units, the land
ownership, and approximate areas of the proposed designated areas for
the Zuni bluehead sucker.
Table 1--Proposed Critical Habitat Units for Zuni Bluehead Sucker
[Area estimates reflect all land within critical habitat unit boundaries]
----------------------------------------------------------------------------------------------------------------
Length of unit
Stream segment Occupied at the time of Land ownership in kilometers
listing (miles)
----------------------------------------------------------------------------------------------------------------
Unit 1--Zuni River Unit
----------------------------------------------------------------------------------------------------------------
Subunit 1a--Zuni River Headwaters
----------------------------------------------------------------------------------------------------------------
Agua Remora............................. Yes....................... Forest Service............ 6.6 (4.1)
Private................... 2.4 (1.5)
Rio Nutria.............................. Yes....................... Zuni Pueblo............... 38.9 (24.2)
Forest Service............ 4.1 (2.6)
State of New Mexico....... 1.8 (1.1)
Private................... 14.2 (8.8)
Tampico Draw............................ Yes....................... Forest Service............ 2.3 (1.4)
Private................... 3.7 (2.3)
Tampico Spring.......................... Yes....................... Private................... 0.2 (0.1)
-----------------------------------------------------------------------
Total............................... .......................... .......................... 74.2 (46.1)
----------------------------------------------------------------------------------------------------------------
Subunit 1b--Zuni River Mainstem
----------------------------------------------------------------------------------------------------------------
Zuni River.............................. No........................ Zuni Pueblo............... 7.4 (4.6)
Rio Pescado............................. No........................ Zuni Pueblo............... 47.3 (29.4)
State of New Mexico....... 5.8 (3.6)
Private................... 15.4 (9.6)
Cebolla Creek........................... No........................ Zuni Pueblo............... 3.7 (2.3)
State of New Mexico....... 0.4 (.02)
Forest Service............ 6.4 (4.0)
Private................... 21.4 (13.3)
-----------------------------------------------------------------------
Total............................... .......................... .......................... 107.8 (67.0)
----------------------------------------------------------------------------------------------------------------
Unit 2--Kinlichee Creek Unit
----------------------------------------------------------------------------------------------------------------
Subunit 2a--Kinlichee Creek
----------------------------------------------------------------------------------------------------------------
Black Soil Wash......................... Yes....................... Navajo Nation............. 21.6 (13.4)
Kinlichee Creek......................... Yes....................... Navajo Nation............. 47.1 (29.3)
Scattered Willow Wash................... Yes....................... Navajo Nation............. 18.2 (11.3)
-----------------------------------------------------------------------
Total............................... .......................... .......................... 86.9 (54.0)
----------------------------------------------------------------------------------------------------------------
Subunit 2b--Red Clay Wash
----------------------------------------------------------------------------------------------------------------
Red Clay Wash........................... No........................ Navajo Nation............. 9.6 (6.0)
----------------------------------------------------------------------------------------------------------------
Unit 3--San Juan River Unit
----------------------------------------------------------------------------------------------------------------
Subunit 3a--Canyon de Chelly
----------------------------------------------------------------------------------------------------------------
Coyote Wash............................. Yes....................... Navajo Nation *........... 6.4 (4.0)
[[Page 5359]]
Crystal Creek........................... Yes....................... Navajo Nation *........... 0.5 (0.3)
Navajo Nation............. 34.2 (21.2)
Sonsela Creek........................... Yes....................... Navajo Nation *........... 19.5 (12.1)
Tsaile Creek............................ Yes....................... Navajo Nation *........... 23.0 (14.3)
Navajo Nation............. 30.6 (19.0)
Wheatfields Creek....................... Yes....................... Navajo Nation *........... 8.5 (5.3)
Navajo Nation............. 29.3 (18.2)
Whiskey Creek........................... Yes....................... Navajo Nation *........... 7.5 (4.7)
Navajo Nation............. 28.1 (17.5)
-----------------------------------------------------------------------
Total............................... .......................... .......................... 187.9 (112.7)
----------------------------------------------------------------------------------------------------------------
Subunit 3b--Little Whiskey Creek
----------------------------------------------------------------------------------------------------------------
Little Whiskey Creek.................... No........................ Navajo Nation............. 8.9 (5.5)
-----------------------------------------------------------------------
Total............................... .......................... .......................... 8.9 (5.5)
----------------------------------------------------------------------------------------------------------------
* These lands are managed by National Park Service in trust for the Navajo Nation.
Note: Area sizes may not sum due to rounding.
We present below brief descriptions of the units and reasons why
the units meet the definition of critical habitat for the Zuni bluehead
sucker.
Unit 1: Zuni River Unit
Subunit 1a--Zuni River Headwaters: Subunit 1a consists of 74.2 km
(46.1 mi) along Agua Remora, Rio Nutria, Tampico Draw, and Tampico
Spring in McKinley County, New Mexico. The land in this subunit is
primarily owned by Zuni Pueblo, Forest Service, and private landowners
with a small amount of State inholdings. The Zuni bluehead sucker
occupies all stream reaches in this subunit, and the subunit contains
all of the primary constituent elements of the physical or biological
features essential to the conservation of the Zuni bluehead sucker.
This unit represents the only remaining headwater spring habitats
occupied by Zuni bluehead sucker.
Livestock grazing is primarily regulated by the Forest Service and
Zuni Pueblo in this subunit; however, trespass livestock grazing may
occur. Additional special management considerations or protection may
be required within Subunit 1a to address low water levels as a result
of water withdrawals and drought, predation from nonnative green
sunfish, and the upstream and downstream effects of impoundments. Such
special management or protection may include maintaining instream
flows, nonnative species removal, and reservoir management that
improves up- and downstream habitat to benefit the Zuni bluehead
sucker.
Subunit 1b--Zuni River Mainstem: Subunit 1b consists of 107.8 km
(67.0 mi) of potential Zuni bluehead sucker habitat along the Zuni
River, Rio Pescado, and Cebolla Creek in McKinley and Cibola Counties,
New Mexico. Land within this subunit is primarily owned by Zuni Pueblo
and private landowners, with a small amount of Forest Service and State
land. The Zuni bluehead sucker historically occupied these streams but
has not been found in the Zuni River or Rio Pescado since the mid-1990s
(NMDGF 2004, p. 5) and has been extirpated from Cebolla Creek since at
least 1979 (Hanson 1980, pp. 29, 34). We consider this unit unoccupied.
When wetted and if suitable habitat were present, the Zuni River and
Rio Pescado could provide important connections between occupied
reaches in Subunit 1a and potential future populations in Cebolla
Creek, which has been identified as containing suitable habitat in the
past and could provide for significant population expansion. Therefore,
this subunit is essential for the conservation of the Zuni bluehead
sucker because it provides for connection between populations and also
provides space for the growth and expansion of the species in this
portion of its historical range.
Unit 2: Kinlichee Creek Unit
Subunit 2a--Kinlichee Creek: Subunit 2a consists of 86.9 km (54.0
mi) along Kinlichee Creek and two tributaries (Black Soil Wash and
Scattered Willow Wash) in Apache County, Arizona. This entire subunit
is located within the Navajo Indian Reservation. The Zuni bluehead
sucker occupies all stream reaches in this subunit, and the subunit
contains all of the primary constituent elements of the physical or
biological features essential to the conservation of the Zuni bluehead
sucker.
Special management considerations or protection may be required
within Subunit 2a to address low water levels as a result of water
withdrawals and drought, sedimentation and riparian vegetation
destruction from road development and livestock grazing, and predation
from nonnative species. Such special management considerations or
protection may include instream flows, stream fencing, erosion control
structures along roads and during construction, reservoir management
that improves up- and downstream habitat to benefit the Zuni bluehead
sucker and nonnative species removal.
Subunit 2b--Red Clay Wash: Subunit 2b consists of 9.6 km (6.0 mi)
of potential Zuni bluehead sucker habitat along Red Clay Wash, in
Apache County, Arizona, on the Navajo Indian Reservation. The Zuni
bluehead sucker historically occupied this stream but does not
currently occur there. Inclusion of Red Clay Wash expands the recovery
potential of the Zuni bluehead sucker in the lower Kinlichee watershed
by increasing population redundancy within the species' historical
range and is therefore essential to the conservation of the species.
Unit 3: San Juan River Unit
Subunit 3a--Canyon de Chelly: Subunit 3a consists of 187.9 km
(112.7 mi) along Tsaile Creek, Wheatfields Creek, Whiskey Creek, Coyote
Wash, Crystal Creek, and Sonsela Creek in
[[Page 5360]]
Apache County, Arizona, and San Juan County, New Mexico. This unit is
located within the Navajo Indian Reservation, portions of which are
managed by the National Park Service as Canyon de Chelly National
Monument in trust for the Navajo Nation. The Zuni bluehead sucker
occupies all stream reaches in this subunit, and the subunit contains
all of the primary constituent elements of the physical or biological
features essential to the conservation of the Zuni bluehead sucker.
Special management considerations or protection may be required
within Subunit 3a to address low water levels as a result of water
withdrawals and drought, sedimentation and riparian vegetation
destruction from road development and livestock grazing, and predation
from nonnative species. Such special management considerations or
protection may include instream flows stream fencing, erosion control
structures along roads and during construction, reservoir management
that improves up- and downstream habitat to benefit the Zuni bluehead
sucker, and nonnative species removal.
Subunit 3b--Little Whiskey Creek: Subunit 3b consists of 8.9 km
(5.5 mi) of potential Zuni bluehead sucker habitat along Little Whiskey
Creek in San Juan County, New Mexico, on the Navajo Indian Reservation.
The Zuni bluehead sucker does not currently occur in Little Whiskey
Creek, but suitable habitat is present and it is reasonable to conclude
the species occurred there historically. Inclusion of Little Whiskey
Creek expands the recovery potential of the Zuni bluehead sucker in the
upper Whiskey Creek watershed by increasing population redundancy
within the species' historical range and is therefore essential to the
conservation of the species.
Effects of Critical Habitat Designation
Section 7 Consultation
Section 7(a)(2) of the Act requires Federal agencies, including the
Service, to ensure that any action they fund, authorize, or carry out
is not likely to jeopardize the continued existence of any endangered
species or threatened species or result in the destruction or adverse
modification of designated critical habitat of such species. In
addition, section 7(a)(4) of the Act requires Federal agencies to
confer with the Service on any agency action which is likely to
jeopardize the continued existence of any species proposed to be listed
under the Act or result in the destruction or adverse modification of
proposed critical habitat.
Decisions by the 5th and 9th Circuit Courts of Appeals have
invalidated our regulatory definition of ``destruction or adverse
modification'' (50 CFR 402.02) (see Gifford Pinchot Task Force v. U.S.
Fish and Wildlife Service, 378 F. 3d 1059 (9th Cir. 2004) and Sierra
Club v. U.S. Fish and Wildlife Service et al., 245 F.3d 434, 442 (5th
Cir. 2001)), and we do not rely on this regulatory definition when
analyzing whether an action is likely to destroy or adversely modify
critical habitat. Under the statutory provisions of the Act, we
determine destruction or adverse modification on the basis of whether,
with implementation of the proposed Federal action, the affected
critical habitat would continue to serve its intended conservation role
for the species.
If a Federal action may affect a listed species or its critical
habitat, the responsible Federal agency (action agency) must enter into
consultation with us. Examples of actions that are subject to the
section 7 consultation process are actions on State, tribal, local, or
private lands that require a Federal permit (such as a permit from the
U.S. Army Corps of Engineers under section 404 of the Clean Water Act
(33 U.S.C. 1251 et seq.) or a permit from the Service under section 10
of the Act) or that involve some other Federal action (such as funding
from the Federal Highway Administration, Federal Aviation
Administration, or the Federal Emergency Management Agency). Federal
actions not affecting listed species or critical habitat, and actions
on State, tribal, local, or private lands that are not federally funded
or authorized, do not require section 7 consultation.
As a result of section 7 consultation, we document compliance with
the requirements of section 7(a)(2) through our issuance of:
(1) A concurrence letter for Federal actions that may affect, but
are not likely to adversely affect, listed species or critical habitat;
or
(2) A biological opinion for Federal actions that may affect and
are likely to adversely affect listed species or critical habitat.
When we issue a biological opinion concluding that a project is
likely to jeopardize the continued existence of a listed species and/or
destroy or adversely modify critical habitat, we provide reasonable and
prudent alternatives to the project, if any are identifiable, that
would avoid the likelihood of jeopardy and/or destruction or adverse
modification of critical habitat. We define ``reasonable and prudent
alternatives'' (at 50 CFR 402.02) as alternative actions identified
during consultation that:
(1) Can be implemented in a manner consistent with the intended
purpose of the action,
(2) Can be implemented consistent with the scope of the Federal
agency's legal authority and jurisdiction,
(3) Are economically and technologically feasible, and
(4) Would, in the Director's opinion, avoid the likelihood of
jeopardizing the continued existence of the listed species and/or avoid
the likelihood of destroying or adversely modifying critical habitat.
Reasonable and prudent alternatives can vary from slight project
modifications to extensive redesign or relocation of the project. Costs
associated with implementing a reasonable and prudent alternative are
similarly variable.
Regulations at 50 CFR 402.16 require Federal agencies to reinitiate
consultation on previously reviewed actions in instances where we have
listed a new species or subsequently designated critical habitat that
may be affected and the Federal agency has retained discretionary
involvement or control over the action (or the agency's discretionary
involvement or control is authorized by law). Consequently, Federal
agencies sometimes may need to request reinitiation of consultation
with us on actions for which formal consultation has been completed, if
those actions with discretionary involvement or control may affect
subsequently listed species or designated critical habitat.
Application of the ``Adverse Modification'' Standard
The key factor related to the adverse modification determination is
whether, with implementation of the proposed Federal action, the
affected critical habitat would continue to serve its intended
conservation role for the species. Activities that may destroy or
adversely modify critical habitat are those that alter the physical or
biological features to an extent that appreciably reduces the
conservation value of critical habitat for the Zuni bluehead sucker. As
discussed above, the role of critical habitat is to support life-
history needs of the species and provide for the conservation of the
species.
Section 4(b)(8) of the Act requires us to briefly evaluate and
describe, in any proposed or final regulation that designates critical
habitat, activities involving a Federal action that may destroy or
adversely modify such
[[Page 5361]]
habitat, or that may be affected by such designation.
Activities that may affect critical habitat, when carried out,
funded, or authorized by a Federal agency, should result in
consultation for the Zuni bluehead sucker. These activities include,
but are not limited to:
(1) Actions that would diminish flows within the active stream
channel. Such activities could include, but are not limited to: Water
diversion, water withdrawal, channelization, construction of any
barriers or impediments within the active stream channel, construction
of permanent or temporary diversion structures, and groundwater pumping
within aquifers associated with the stream or springs. These activities
could affect water depth, velocity, and flow patterns, all of which are
essential to the different life stages of Zuni bluehead sucker.
(2) Actions that would significantly increase sediment deposition
within a stream channel. Such activities could include, but are not
limited to: Excessive sedimentation from livestock grazing, road
construction, commercial or urban development, channel alteration,
timber harvest, or other watershed and floodplain disturbances. These
activities could adversely affect reproduction of the species by
preventing hatching of eggs through suffocation, or by eliminating
suitable habitat for egg placement by Zuni bluehead sucker. In
addition, excessive levels of sedimentation reduce or eliminate algae
production and can make it difficult for the Zuni bluehead sucker to
locate prey.
(3) Actions that result in the introduction, spread, or
augmentation of nonnative aquatic species in occupied stream segments,
or in stream segments that are hydrologically connected to occupied
stream segments, even if those segments are occasionally intermittent,
or introduction of other species that compete with or prey on Zuni
bluehead sucker. Possible actions could include, but are not limited
to: Stocking of nonnative fishes, stocking of sport fish, or other
related actions. These activities can introduce parasites or disease,
or affect the growth, reproduction, and survival of Zuni bluehead
sucker.
(4) Actions that would significantly alter channel morphology. Such
activities could include, but are not limited to: Channelization,
impoundment, road and bridge construction, mining, dredging, and
destruction of riparian vegetation. These activities may lead to
changes in water flows and levels that would degrade or eliminate the
Zuni bluehead, their habitats, or both. These actions can also lead to
increased sedimentation and degradation of the water.
(5) Actions that significantly alter the water chemistry of the
active channel. Such activities could include release of chemicals,
biological pollutants, or other substances into the surface water or
connected groundwater at a point source or by dispersed release
(nonpoint source), and storage of chemicals or pollutants that can be
transmitted, via surface water, groundwater, or air, into critical
habitat. These actions can affect water chemistry and the prey base of
the Zuni bluehead sucker.
Exemptions
Application of Section 4(a)(3) of the Act
The Sikes Act Improvement Act of 1997 (Sikes Act) (16 U.S.C. 670a)
required each military installation that includes land and water
suitable for the conservation and management of natural resources to
complete an integrated natural resources management plan (INRMP) by
November 17, 2001. An INRMP integrates implementation of the military
mission of the installation with stewardship of the natural resources
found on the base. Each INRMP includes:
(1) An assessment of the ecological needs on the installation,
including the need to provide for the conservation of listed species;
(2) A statement of goals and priorities;
(3) A detailed description of management actions to be implemented
to provide for these ecological needs; and
(4) A monitoring and adaptive management plan.
Among other things, each INRMP must, to the extent appropriate and
applicable, provide for fish and wildlife management; fish and wildlife
habitat enhancement or modification; wetland protection, enhancement,
and restoration where necessary to support fish and wildlife; and
enforcement of applicable natural resource laws.
The National Defense Authorization Act for Fiscal Year 2004 (Pub.
L. 108-136) amended the Act to limit areas eligible for designation as
critical habitat. Specifically, section 4(a)(3)(B)(i) of the Act (16
U.S.C. 1533(a)(3)(B)(i)) now provides: ``The Secretary shall not
designate as critical habitat any lands or other geographic areas owned
or controlled by the Department of Defense, or designated for its use,
that are subject to an integrated natural resources management plan
prepared under section 101 of the Sikes Act (16 U.S.C. 670a), if the
Secretary determines in writing that such plan provides a benefit to
the species for which critical habitat is proposed for designation.''
There are no Department of Defense lands within the proposed
critical habitat designation for Zuni bluehead sucker.
Exclusions
Application of Section 4(b)(2) of the Act
Section 4(b)(2) of the Act states that the Secretary shall
designate and make revisions to critical habitat on the basis of the
best available scientific data after taking into consideration the
economic impact, national security impact, and any other relevant
impact of specifying any particular area as critical habitat. The
Secretary may exclude an area from critical habitat if he determines
that the benefits of such exclusion outweigh the benefits of specifying
such area as part of the critical habitat, unless he determines, based
on the best scientific data available, that the failure to designate
such area as critical habitat will result in the extinction of the
species. In making that determination, the statute on its face, as well
as the legislative history, are clear that the Secretary has broad
discretion regarding which factor(s) to use and how much weight to give
to any factor.
Under section 4(b)(2) of the Act, we may exclude an area from
designated critical habitat based on economic impacts, impacts on
national security, or any other relevant impacts. In considering
whether to exclude a particular area from the designation, we identify
the benefits of including the area in the designation, identify the
benefits of excluding the area from the designation, and evaluate
whether the benefits of exclusion outweigh the benefits of inclusion.
If the analysis indicates that the benefits of exclusion outweigh the
benefits of inclusion, the Secretary may exercise his discretion to
exclude the area only if such exclusion would not result in the
extinction of the species.
Exclusions Based on Economic Impacts
Under section 4(b)(2) of the Act, we consider the economic impacts
of specifying any particular area as critical habitat. In order to
consider economic impacts, we are preparing an analysis of the economic
impacts of the proposed critical habitat designation and related
factors. Potential land use sectors that may be affected by the Zuni
bluehead sucker critical habitat designation include water diversion or
impoundment repairs, forest management (silvicultural practices), fire
suppression activities, road development, grazing, groundwater
[[Page 5362]]
withdrawals, and subdivision development. We also consider any social
impacts that might occur because of the designation.
During the development of a final designation, we will consider
economic impacts based on information in our economic analysis, public
comments, and other new information, and areas may be excluded from the
final critical habitat designation under section 4(b)(2) of the Act and
our implementing regulations at 50 CFR 424.19.
Exclusions Based on National Security Impacts
Under section 4(b)(2) of the Act, we consider whether there are
lands where a national security impact might exist. In preparing this
proposal, we have determined that the lands within the proposed
designation of critical habitat for the Zuni bluehead sucker are not
owned or managed by the Department of Defense, and, therefore, we
anticipate no impact on national security. Consequently, the Secretary
is not intending to exercise his discretion to exclude any areas from
the final designation based on impacts on national security.
Exclusions Based on Other Relevant Impacts
Under section 4(b)(2) of the Act, we consider any other relevant
impacts, in addition to economic impacts and impacts on national
security. We consider a number of factors including whether the
landowners have developed any HCPs or other management plans for the
area, or whether there are conservation partnerships that would be
encouraged by designation of, or exclusion from, critical habitat. In
addition, we look at any tribal issues, and consider the government-to-
government relationship of the United States with tribal entities. We
also consider any social impacts that might occur because of the
designation.
When we evaluate the existence of a conservation plan when
considering the benefits of exclusion, we consider a variety of
factors, including but not limited to, whether the plan is finalized;
how it provides for the conservation of the essential physical or
biological features; whether there is a reasonable expectation that the
conservation management strategies and actions contained in a
management plan will be implemented into the future; whether the
conservation strategies in the plan are likely to be effective; and
whether the plan contains a monitoring program or adaptive management
to ensure that the conservation measures are effective and can be
adapted in the future in response to new information.
There are tribal lands included in the proposed designation of
critical habitat for the Zuni bluehead sucker. Using the criteria found
in the Criteria Used To Identify Critical Habitat section, we have
determined that tribal lands that are occupied by the Zuni bluehead
sucker contain the features essential for the conservation the species,
as well as tribal lands unoccupied by the Zuni bluehead sucker that are
essential for the conservation of the species. We have begun
government-to-government consultation with these tribes, and will
continue to do so throughout the public comment period and during
development of the final designation of critical habitat for the Zuni
bluehead sucker. We will consider these areas for exclusion from the
final critical habitat designation to the extent consistent with the
requirements of section 4(b)(2) of the Act. The Navajo Nation and Zuni
Pueblo are the main tribes affected by this proposed rule. We sent
notification letters in July 2012 to both tribes describing the
exclusion process under section 4(b)(2) of the Act, and we have engaged
in conversations with both tribes about the proposal to the extent
possible without disclosing predecisional information. We coordinated
with the Navajo Nation in May 2012, to coordinate surveys on Navajo
lands. Additionally, we are working with Zuni Pueblo to develop a
management plan for their lands. We will schedule a meeting with the
tribes and any other interested tribes shortly after publication of
this proposed rule so that we can give them as much time as possible to
comment.
A final determination on whether the Secretary will exercise his
discretion to exclude any of these areas from critical habitat for the
Zuni bluehead sucker will be made when we publish the final rule
designating critical habitat. We will take into account public comments
and carefully weigh the benefits of exclusion versus inclusion of these
areas. We may also consider areas not identified above for exclusion
from the final critical habitat designation based on information we may
receive during the preparation of the final rule (e.g., management
plans for additional areas).
Peer Review
In accordance with our joint policy on peer review published in the
Federal Register on July 1, 1994 (59 FR 34270), we will seek the expert
opinions of at least three appropriate and independent specialists
regarding this proposed rule. The purpose of peer review is to ensure
that our listing determination and critical habitat designation are
based on scientifically sound data, assumptions, and analyses. We have
invited these peer reviewers to comment during this public comment
period.
We will consider all comments and information received during this
comment period on this proposed rule during our preparation of a final
determination. Accordingly, the final decision may differ from this
proposal.
Public Hearings
Section 4(b)(5) of the Act provides for one or more public hearings
on this proposal, if requested. Requests must be received within 45
days after the date of publication of this proposed rule in the Federal
Register. Such requests must be sent to the address shown in the FOR
FURTHER INFORMATION CONTACT section. We will schedule public hearings
on this proposal, if any are requested, and announce the dates, times,
and places of those hearings, as well as how to obtain reasonable
accommodations, in the Federal Register and local newspapers at least
15 days before the hearing.
Required Determinations
Regulatory Planning and Review--Executive Orders 12866 and 13563
Executive Order 12866 provides that the Office of Information and
Regulatory Affairs will review all significant rules. The Office of
Information and Regulatory Affairs has determined that this rule is not
significant.
Executive Order 13563 reaffirms the principles of Executive Order
12866 while calling for improvements in the nation's regulatory system
to promote predictability, to reduce uncertainty, and to use the best,
most innovative, and least burdensome tools for achieving regulatory
ends. The executive order directs agencies to consider regulatory
approaches that reduce burdens and maintain flexibility and freedom of
choice for the public where these approaches are relevant, feasible,
and consistent with regulatory objectives. Executive Order 13563
emphasizes further that regulations must be based on the best available
science and that the rulemaking process must allow for public
participation and an open exchange of ideas. We have developed this
rule in a manner consistent with these requirements.
Regulatory Flexibility Act (5 U.S.C. 601 et seq.)
Under the Regulatory Flexibility Act (RFA; 5 U.S.C. 601 et seq.) as
amended by the Small Business Regulatory Enforcement Fairness Act
(SBREFA) of 1996 (5 U.S.C 801 et seq.), whenever an
[[Page 5363]]
agency must publish a notice of rulemaking for any proposed or final
rule, it must prepare and make available for public comment a
regulatory flexibility analysis that describes the effects of the rule
on small entities (small businesses, small organizations, and small
government jurisdictions). However, no regulatory flexibility analysis
is required if the head of the agency certifies the rule will not have
a significant economic impact on a substantial number of small
entities. The SBREFA amended the RFA to require Federal agencies to
provide a certification statement of the factual basis for certifying
that the rule will not have a significant economic impact on a
substantial number of small entities.
According to the Small Business Administration, small entities
include small organizations such as independent nonprofit
organizations; small governmental jurisdictions, including school
boards and city and town governments that serve fewer than 50,000
residents; and small businesses (13 CFR 121.201). Small businesses
include such businesses as manufacturing and mining concerns with fewer
than 500 employees, wholesale trade entities with fewer than 100
employees, retail and service businesses with less than $5 million in
annual sales, general and heavy construction businesses with less than
$27.5 million in annual business, special trade contractors doing less
than $11.5 million in annual business, and forestry and logging
operations with fewer than 500 employees and annual business less than
$7 million. To determine whether small entities may be affected, we
will consider the types of activities that might trigger regulatory
impacts under this designation as well as types of project
modifications that may result. In general, the term ``significant
economic impact'' is meant to apply to a typical small business firm's
business operations.
Importantly, the incremental impacts of a rule must be both
significant and substantial to prevent certification of the rule under
the RFA and to require the preparation of an initial regulatory
flexibility analysis. If a substantial number of small entities are
affected by the proposed critical habitat designation, but the per-
entity economic impact is not significant, the Service may certify.
Likewise, if the per-entity economic impact is likely to be
significant, but the number of affected entities is not substantial,
the Service may also certify.
The Service's current understanding of recent case law is that
Federal agencies are only required to evaluate the potential impacts of
rulemaking on those entities directly regulated by the rulemaking;
therefore, they are not required to evaluate the potential impacts to
those entities not directly regulated. The designation of critical
habitat for an endangered or threatened species only has a regulatory
effect where a Federal action agency is involved in a particular action
that may affect the designated critical habitat. Under these
circumstances, only the Federal action agency is directly regulated by
the designation, and, therefore, consistent with the Service's current
interpretation of RFA and recent case law, the Service may limit its
evaluation of the potential impacts to those identified for Federal
action agencies. Under this interpretation, there is no requirement
under the RFA to evaluate the potential impacts to entities not
directly regulated, such as small businesses. However, Executive Orders
12866 and 13563 direct Federal agencies to assess costs and benefits of
available regulatory alternatives in quantitative (to the extent
feasible) and qualitative terms. Consequently, it is the current
practice of the Service to assess to the extent practicable these
potential impacts if sufficient data are available, whether or not this
analysis is believed by the Service to be strictly required by the RFA.
In other words, while the effects analysis required under the RFA is
limited to entities directly regulated by the rulemaking, the effects
analysis under the Act, consistent with the EO regulatory analysis
requirements, can take into consideration impacts to both directly and
indirectly impacted entities, where practicable and reasonable.
In conclusion, we believe that, based on our interpretation of
directly regulated entities under the RFA and relevant case law, this
designation of critical habitat will only directly regulate Federal
agencies which are not by definition small business entities. And as
such, we certify that, if promulgated, this designation of critical
habitat would not have a significant economic impact on a substantial
number of small business entities. Therefore, an initial regulatory
flexibility analysis is not required. However, though not necessarily
required by the RFA, in our draft economic analysis for this proposal
we will consider and evaluate the potential effects to third parties
that may be involved with consultations with Federal action agencies
related to this action.
Energy Supply, Distribution, or Use--Executive Order 13211
Executive Order 13211 (Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use) requires
agencies to prepare Statements of Energy Effects when undertaking
certain actions. We do not expect the designation of this proposed
critical habitat to significantly affect energy supplies, distribution,
or use. Therefore, this action is not a significant energy action, and
no Statement of Energy Effects is required. However, we will further
evaluate this issue as we conduct our economic analysis, and review and
revise this assessment as warranted.
Unfunded Mandates Reform Act (2 U.S.C. 1501 et seq.)
In accordance with the Unfunded Mandates Reform Act (2 U.S.C. 1501
et seq.), we make the following findings:
(1) This proposed rule will not produce a Federal mandate. In
general, a Federal mandate is a provision in legislation, statute, or
regulation that would impose an enforceable duty upon State, local, or
tribal governments, or the private sector, and includes both ``Federal
intergovernmental mandates'' and ``Federal private sector mandates.''
These terms are defined in 2 U.S.C. 658(5)-(7). ``Federal
intergovernmental mandate'' includes a regulation that ``would impose
an enforceable duty upon State, local, or tribal governments'' with two
exceptions. It excludes ``a condition of Federal assistance.'' It also
excludes ``a duty arising from participation in a voluntary Federal
program,'' unless the regulation ``relates to a then-existing Federal
program under which $500,000,000 or more is provided annually to State,
local, and tribal governments under entitlement authority,'' if the
provision would ``increase the stringency of conditions of assistance''
or ``place caps upon, or otherwise decrease, the Federal Government's
responsibility to provide funding,'' and the State, local, or tribal
governments ``lack authority'' to adjust accordingly. At the time of
enactment, these entitlement programs were: Medicaid; Aid to Families
with Dependent Children work programs; Child Nutrition; Food Stamps;
Social Services Block Grants; Vocational Rehabilitation State Grants;
Foster Care, Adoption Assistance, and Independent Living; Family
Support Welfare Services; and Child Support Enforcement. ``Federal
private sector mandate'' includes a regulation that ``would impose an
enforceable duty upon the private sector, except (i) a
[[Page 5364]]
condition of Federal assistance or (ii) a duty arising from
participation in a voluntary Federal program.''
The designation of critical habitat does not impose a legally
binding duty on non-Federal Government entities or private parties.
Under the Act, the only regulatory effect is that Federal agencies must
ensure that their actions do not destroy or adversely modify critical
habitat under section 7. While non-Federal entities that receive
Federal funding, assistance, or permits, or that otherwise require
approval or authorization from a Federal agency for an action, may be
indirectly impacted by the designation of critical habitat, the legally
binding duty to avoid destruction or adverse modification of critical
habitat rests squarely on the Federal agency. Furthermore, to the
extent that non-Federal entities are indirectly impacted because they
receive Federal assistance or participate in a voluntary Federal aid
program, the Unfunded Mandates Reform Act would not apply, nor would
critical habitat shift the costs of the large entitlement programs
listed above onto State governments.
(2) We lack the available economic information to determine if a
Small Government Agency Plan is required. Therefore, we defer this
finding until completion of the draft economic analysis is prepared
under section 4(b)(2) of the Act.
Takings--Executive Order 12630
In accordance with Executive Order 12630 (Government Actions and
Interference with Constitutionally Protected Private Property Rights),
we will analyze the potential takings implications of designating
critical habitat for the Zuni bluehead sucker in a takings implications
assessment. The draft economic analysis will provide the foundation for
us to use in preparing a takings implication assessment. Critical
habitat designation does not affect landowner actions that do not
require Federal funding or permits, nor does it preclude development of
habitat conservation programs or issuance of incidental take permits to
permit actions that do require Federal funding or permits to go
forward.
Federalism--Executive Order 13132
In accordance with Executive Order 13132 (Federalism), this
proposed rule does not have significant Federalism effects. A
Federalism assessment is not required. In keeping with Department of
the Interior and Department of Commerce policy, we requested
information from, and coordinated development of, this proposed
critical habitat designation with appropriate State resource agencies
in New Mexico and Arizona. The designation of critical habitat in areas
currently occupied by the Zuni bluehead sucker imposes no additional
restrictions to those currently in place and, therefore, has little
incremental impact on State and local governments and their activities.
The designation may have some benefit to these governments because the
areas that contain the physical or biological features essential to the
conservation of the species are more clearly defined, and the elements
of the features of the habitat necessary to the conservation of the
species are specifically identified. This information does not alter
where and what federally sponsored activities may occur. However, it
may assist local governments in long-range planning (rather than having
them wait for case-by-case section 7 consultations to occur).
Where State and local governments require approval or authorization
from a Federal agency for actions that may affect critical habitat,
consultation under section 7(a)(2) would be required. While non-Federal
entities that receive Federal funding, assistance, or permits, or that
otherwise require approval or authorization from a Federal agency for
an action, may be indirectly impacted by the designation of critical
habitat, the legally binding duty to avoid destruction or adverse
modification of critical habitat rests squarely on the Federal agency.
Civil Justice Reform--Executive Order 12988
In accordance with Executive Order 12988 (Civil Justice Reform),
the Office of the Solicitor has determined that the rule does not
unduly burden the judicial system and that it meets the requirements of
sections 3(a) and 3(b)(2) of the Order. We are designating critical
habitat in accordance with the provisions of the Act. To assist the
public in understanding the habitat needs of the species, the rule
identifies the elements of physical or biological features essential to
the conservation of the species. The designated areas of critical
habitat are presented on maps, and the rule provides several options
for the interested public to obtain more detailed location information,
if desired.
Paperwork Reduction Act of 1995 (44 U.S.C. 3501 et seq.)
This rule does not contain any new collections of information that
require approval by OMB under the Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.). This rule will not impose recordkeeping or
reporting requirements on State or local governments, individuals,
businesses, or organizations. An agency may not conduct or sponsor, and
a person is not required to respond to, a collection of information
unless it displays a currently valid OMB control number.
National Environmental Policy Act (42 U.S.C. 4321 et seq.)
It is our position that, outside the jurisdiction of the U.S. Court
of Appeals for the Tenth Circuit, we do not need to prepare
environmental analyses pursuant to NEPA in connection with designating
critical habitat under the Endangered Species Act. We published a
notice outlining our reasons for this determination in the Federal
Register on October 25, 1983 (48 FR 49244). This position was upheld by
the U.S. Court of Appeals for the Ninth Circuit (Douglas County v.
Babbitt, 48 F.3d 1495 (9th Cir. 1995), cert. denied 516 U.S. 1042
(1996)). However, when the range of the species includes States within
the Tenth Circuit, such as that of the Zuni bluehead sucker, under the
Tenth Circuit ruling in Catron County Board of Commissioners v. U.S.
Fish and Wildlife Service, 75 F.3d 1429 (10th Cir. 1996), we will
undertake a NEPA analysis for critical habitat designation and notify
the public of the availability of the draft environmental assessment
for this proposal when it is finished.
Government-to-Government Relationship With Tribes
In accordance with the President's memorandum of April 29, 1994
(Government-to-Government Relations with Native American Tribal
Governments; 59 FR 22951), Executive Order 13175 (Consultation and
Coordination With Indian Tribal Governments), and the Department of the
Interior's manual at 512 DM 2, we readily acknowledge our
responsibility to communicate meaningfully with recognized Federal
Tribes on a government-to-government basis. In accordance with
Secretarial Order 3206 of June 5, 1997 (American Indian Tribal Rights,
Federal-Tribal Trust Responsibilities, and the Endangered Species Act),
we readily acknowledge our responsibilities to work directly with
tribes in developing programs for healthy ecosystems, to acknowledge
that tribal lands are not subject to the same controls as Federal
public lands, to remain sensitive to Indian culture, and to make
information available to tribes.
There are tribal lands in Arizona and New Mexico included in this
proposed designation of critical habitat. Using the criteria found in
the Criteria Used To Identify Critical Habitat section, we
[[Page 5365]]
have determined that there are tribal lands that are occupied by the
Zuni bluehead sucker that contain the features essential for the
conservation of the species, as well as tribal lands unoccupied by the
species at the time of listing that are essential for the conservation
of the Zuni bluehead sucker. We have begun government-to-government
consultation with these tribes throughout the public comment period and
during development of the final designation of Zuni bluehead sucker
critical habitat. We will consider these areas for exclusion from the
final critical habitat designation to the extent consistent with the
requirements of section 4(b)(2) of the Act. The Navajo Nation and Zuni
Pueblo are the main tribes affected by this proposed rule. We sent
notification letters in July 2012 to each tribe describing the
exclusion process under section 4(b)(2) of the Act, and we have engaged
in conversations with both tribes about the proposal to the extent
possible without disclosing predecisional information. We coordinated
with the Navajo Nation in May 2012 to coordinate surveys on Navajo
lands. Additionally, we are working with Zuni Pueblo to develop a
management plan for their lands. We will schedule meetings with these
tribes and any other interested tribes shortly after publication of
this proposed rule so that we can give them as much time as possible to
comment.
Clarity of the Rule
We are required by Executive Orders 12866 and 12988 and by the
Presidential Memorandum of June 1, 1998, to write all rules in plain
language. This means that each rule we publish must:
(1) Be logically organized;
(2) Use the active voice to address readers directly;
(3) Use clear language rather than jargon;
(4) Be divided into short sections and sentences; and
(5) Use lists and tables wherever possible.
If you feel that we have not met these requirements, send us
comments by one of the methods listed in the ADDRESSES section. To
better help us revise the rule, your comments should be as specific as
possible. For example, you should tell us the numbers of the sections
or paragraphs that are unclearly written, which sections or sentences
are too long, the sections where you feel lists or tables would be
useful, etc.
References Cited
A complete list of references cited in this rulemaking is available
on the Internet at https://www.regulations.gov and upon request from the
New Mexico Ecological Services Field Office (see FOR FURTHER
INFORMATION CONTACT).
Authors
The primary authors of this proposed rule are the staff members of
the New Mexico Ecological Services Field Office.
List of Subjects in 50 CFR Part 17
Endangered and threatened species, Exports, Imports, Reporting and
recordkeeping requirements, Transportation.
Proposed Regulation Promulgation
Accordingly, we propose to amend part 17, subchapter B of chapter
I, title 50 of the Code of Federal Regulations, as set forth below:
PART 17--[AMENDED]
0
1. The authority citation for part 17 continues to read as follows:
Authority: 16 U.S.C. 1361-1407; 1531-1544; and 4201-4245, unless
otherwise noted.
0
2. In Sec. 17.95, amend paragraph (e) by adding an entry for ``Zuni
bluehead sucker (Catostomus discobolus yarrowi),'' after the entry for
``Warner Sucker (Catostomus warnerensis)'' to read as follows:
Sec. 17.95 Critical habitat--fish and wildlife.
* * * * *
(e) Fishes.
* * * * *
Zuni bluehead sucker (Catostomus discobolus yarrowi)
(1) Critical habitat units are depicted for Apache County, Arizona,
and Cibola, McKinley, and San Juan Counties, New Mexico, on the maps
below.
(2) Within these areas, the primary constituent elements of the
physical or biological features essential to the conservation of the
Zuni bluehead sucker consist of three components:
(i) A riverine system with habitat to support all life stages of
Zuni bluehead sucker, which includes:
(A) Dynamic flows that allow for periodic changes in channel
morphology and adequate river functions, such as channel reshaping and
delivery of coarse sediments.
(B) Stream courses with perennial flows, or areas that may be
periodically dewatered but serve as connective corridors between
occupied or seasonally occupied habitat and through which the species
may move when the habitat is wetted.
(C) Stream microhabitat types including runs, riffles, and pools
with substrate ranging from gravel, cobble and bedrock substrates with
low or moderate amounts of fine sediment and substrate embeddedness.
(D) Streams with depths generally less than 2 m (3.3 ft), and with
slow to swift flow velocities less than 35 cm/sec (1.1 ft/sec).
(E) Clear, cool water with low turbidity and temperatures in the
general range of 9.0 to 28.0 [deg]C (48.2 to 82.4 [deg]F).
(F) No harmful levels of pollutants.
(G) Adequate riparian shading to reduce water temperatures when
ambient temperatures are high and provide protective cover from
predators.
(ii) An abundant aquatic insect food base consisting of fine
particulate organic material, filamentous algae, midge larvae,
caddisfly larvae, mayfly larvae, flatworms, and small terrestrial
insects.
(iii) Areas devoid of nonnative aquatic species or areas that are
maintained to kept nonnatives at a level that allows the Zuni bluehead
sucker to continue to survive and reproduce.
(3) Critical habitat does not include manmade structures (such as
bridges, docks, and aqueducts) and the land on which they are located
existing within the legal boundaries on [DATE 30 DAYS AFTER THE DATE OF
PUBLICATION OF THE FINAL RULE IN THE Federal Register].
(4) Critical habitat map units. Data layers defining map units were
created on a base of USGS digital ortho-photo quarter-quadrangles, and
critical habitat units were then mapped using Universal Transverse
Mercator (UTM) Zone 15N coordinates. The maps in this entry, as
modified by any accompanying regulatory text, establish the boundaries
of the critical habitat designation. The coordinates or plot points or
both on which each map is based are available to the public at the
Service's Internet site, (https://www.fws.gov/southwest/es/NewMexico/),
(https://www.regulations.gov at Docket No. FWS-R2-ES-2013-002 and at the
New Mexico Ecological Services Field Office. You may obtain field
office location information by contacting one of the Service regional
offices, the addresses of which are listed at 50 CFR part 22.
(5) Note: Index of critical habitat units for the Zuni bluehead
sucker follows:
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[[Page 5366]]
[GRAPHIC] [TIFF OMITTED] TP25JA13.012
(6) Unit 1: Zuni River Unit, McKinley and Cibola Counties, New
Mexico. Map of Unit 1 follows:
[[Page 5367]]
[GRAPHIC] [TIFF OMITTED] TP25JA13.013
(7) Unit 2: Kinlichee Creek Unit, Apache County, Arizona, and
McKinley and San Juan Counties, New Mexico. Map of Unit 2 follows:
[[Page 5368]]
[GRAPHIC] [TIFF OMITTED] TP25JA13.014
[[Page 5369]]
(8) Unit 3: San Juan River Unit, Apache County, Arizona, and San
Juan County, New Mexico. Map of Unit 3 is provided at paragraph (7) of
this entry.
* * * * *
Dated: January 15, 2013.
Michael Bean,
Acting Principal Deputy Assistant Secretary for Fish Wildlife and
Parks.
[FR Doc. 2013-01302 Filed 1-24-13; 8:45 am]
BILLING CODE 4310-55-P