[Federal Register Volume 86, Number 130 (Monday, July 12, 2021)]
[Notices]
[Pages 36570-36572]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2021-14733]


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DEPARTMENT OF THE INTERIOR

Fish and Wildlife Service

[Docket No. FWS-R2-ES-2020-0040; FXES11130200000-201-FF02ENEH00]


Endangered and Threatened Wildlife and Plants; Draft Revised 
Recovery Plan for Gila Trout

AGENCY: Fish and Wildlife Service, Interior.

ACTION: Notice of availability; request for comment.

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SUMMARY: We, the U.S. Fish and Wildlife Service, announce the 
availability of our draft revised recovery plan for the Gila trout, 
listed as threatened under the Endangered Species Act. This fish 
species is endemic to mountain streams within the upper Gila River 
basin in New Mexico and Arizona. We provide this notice to seek 
comments from the public and Federal, Tribal, State, and local 
governments.

DATES: We must receive written comments on or before September 10, 
2021.

ADDRESSES: 
    Reviewing Documents: You may obtain a copy of the draft revised 
recovery plan and recovery implementation strategy in Docket No. FWS-
R2-ES-2020-0040 at http://www.regulations.gov.
    Submitting Comments: You may submit comments by one of the 
following methods:
    <bullet> Federal eRulemaking Portal: http://www.regulations.gov. 
Follow the instructions for submitting comments on Docket No. FWS-R2-
ES-2020-0040.
    <bullet> U.S.: Public Comments Processing; Attn: Docket No. FWS-R2-
ES-2019-0040; U.S. Fish and Wildlife Service Headquarters, MS: PRB/3W; 
5275 Leesburg Pike, Falls Church, VA 22041-3803.
    For additional information about submitting comments, see Request 
for Public Comments and Public Availability of Comments under 
SUPPLEMENTARY INFORMATION.

FOR FURTHER INFORMATION CONTACT: Shawn Sartorius, Field Supervisor, New 
Mexico Ecological Services Field Office, by phone at 505-761-4781, by 
email at <a href="/cdn-cgi/l/email-protection#6d0300081e0b022d0b1a1e430a021b"><span class="__cf_email__" data-cfemail="83edeee6f0e5ecc3e5f4f0ade4ecf5">[email protected]</span></a>, or via the Federal Relay Service at 800-877-
8339 for TTY service.

SUPPLEMENTARY INFORMATION: We, the U.S. Fish and Wildlife Service 
(Service), announce the availability of our draft revised recovery plan 
for the Gila trout (Oncorhynchus gilae), listed as threatened under the 
Endangered Species Act of 1973, as amended (ESA; 16 U.S.C. 1531 et 
seq.). Gila trout are endemic to mountain streams in the Gila, San 
Francisco, Agua Fria, and Verde River drainages in New Mexico and 
Arizona. The draft revised recovery plan includes site-specific 
management actions and objective, measurable criteria that, when met, 
will enable us to remove the Gila trout from the list of endangered and 
threatened wildlife. We request review and comment on this plan from 
local, State, and Federal agencies; Tribes; and the public. We will 
also accept any new information on the status of the Gila trout 
throughout its range to assist in finalizing the recovery plan.

Background

    Recovery of endangered or threatened animals and plants to the 
point where they are again secure, self-sustaining members of their 
ecosystems is a primary goal of our endangered species program and the 
ESA. Recovery means improvement of the status of listed species to the 
point at which listing is no longer appropriate under the criteria set 
out in section 4(a)(1) of the ESA. The ESA requires the development of 
recovery plans for listed species, unless such a plan would not promote 
the conservation of a particular species. The Service approved the 
original recovery plan for the Gila trout on January 12, 1979 (Service 
1979), with subsequent revisions approved on January 3, 1984 (Service 
1984), December 8, 1993 (Service 1993), and August 19, 2003 (Service 
2003).
    This draft revised recovery plan for the Gila trout represents the 
fourth revision and considers updated information on genetics, 
population status, and threats (principally wildfire effects and 
hybridization) in the development of revised recovery objectives, 
criteria, and actions. We used a streamlined approach to recovery 
planning and implementation for the Gila trout by preparing separate 
recovery plan and recovery implementation strategy documents. The 
information in the draft recovery plan provides the biological 
background, a threats assessment, a strategy for recovery of the Gila 
trout, quantitative delisting criteria, a list of prioritized recovery 
actions, and the estimated time and cost to recovery (Service 2020a). 
The separate recovery implementation strategy document further 
describes in detail the specific activities needed to implement the 
recovery actions (Service 2020b).

Summary of Species Information

    Gila trout are endemic to mountain streams within the Gila, San 
Francisco, Agua Fria, and Verde River drainages in New Mexico and 
Arizona. Although Gila trout were documented to occur in the upper Gila 
River basin since at least 1885, the species was not described until 
1950, by which time its distribution had been dramatically reduced. On 
March 11, 1967, we listed the Gila trout as endangered under the 
Federal Endangered Species Preservation Act of 1966 (32 FR 4001). The 
Gila trout's endangered status was continued under the Endangered 
Species Act of 1973, and we reclassified it as a threatened species on 
July 18, 2006, with a special rule under section 4(d) of the ESA (71 FR 
40657).
    Gila trout are readily identified by their iridescent gold sides, 
which blend to a darker shade of copper on the opercles (bony plates 
surrounding the gills). Spots on the body are small and profuse, 
generally occurring above the lateral line and extending onto the head, 
dorsal fin, and caudal fin. These spots are irregularly shaped on the 
sides and increase in size dorsally. A few scattered spots are 
sometimes present on the anal fin, and the adipose fin is typically 
large and well spotted. Dorsal, pelvic, and anal fins have a white to 
yellowish tip that may extend along the leading edge of the pelvic 
fins. A yellow cutthroat mark is present on most mature specimens. Parr 
marks (vertical bars present when trout are less than a year old) are 
commonly retained by adults, and a faint, salmon-pink band is also 
present on adults, particularly during spawning season, when the 
normally white belly may be streaked with yellow or reddish orange. 
Spawning of Gila trout occurs mainly in April and begins when water 
temperatures reach about 8 [deg]C (46 [deg]F), but day length may also 
be an important cue. Gila trout fry [20 to 25 millimeters (mm), or 0.8 
to 1.0 inches (in) total length] emerge in 56 to 70 days. Females reach 
maturity between two to four years after hatching, and males typically 
reach maturity at two or three years. Most individuals are mature at a 
length of 150 mm (6 in) or greater, and live five years. Thus, the 
majority of adult female Gila trout spawn only twice before

[[Page 36571]]

dying, and most adult males only spawn three or four times before 
dying.
    Gila trout require perennial streamflow and coldwater aquatic 
habitats with unimpaired water quality to maintain persistent, viable 
populations. Flow regimes vary depending on the site-specific 
characteristics of stream reaches (e.g., stream gradient, seepage, 
substrate composition, channel dimensions, and watershed hydrology). 
Suitable water temperature regimes are characterized by maximum water 
temperatures that do not exceed approximately 20 [deg]C (68 [deg]F) for 
six or more consecutive hours in a 24-hour period on more than three 
consecutive days, and maximum temperature that do not exceed 24 [deg]C 
(77 [deg]F). Suitable water quality for Gila trout is characterized by 
high dissolved oxygen concentration, low turbidity and conductivity, 
low levels of total dissolved solids, near-neutral pH, and low 
conductivity. In addition to perennial stream flow and suitable water 
temperature and water quality, Gila trout require a diversity of 
habitats sufficient to sustain all life stages of the species (i.e., 
eggs, fry, juveniles, and adults). This includes suitable spawning 
habitat, habitat where fry can find shelter and food, and areas 
suitable for occupancy by juvenile and adult Gila trout. Sufficient 
pool habitat and spawning habitat are likely the two most important 
habitat features with respect to Gila trout population persistence.
    Fragmentation of the historical distribution of Gila trout has 
resulted in several populations confined to small, isolated habitats 
throughout the range of the species. Collections from streams in the 
upper Gila River Basin and San Francisco River Basin, along with 
genetic analyses, indicate that five lineages of Gila trout exist: Main 
Diamond Creek, South Diamond Creek, Whiskey Creek, Spruce Creek, and 
Iron Creek. The distribution of these lineages has fluctuated since 
1975, when only five remnant populations (i.e., a self-sustaining group 
of Gila trout inhabiting a single stream) were known. Currently, there 
are 17 extant populations of Gila trout inhabiting approximately 137.5 
km (85.2 mi) of stream habitat. These include five populations of the 
Main Diamond Creek lineage, four populations of the South Diamond Creek 
lineage, three populations of the Whiskey Creek lineage, two 
populations of the Spruce Creek lineage, two populations of the Iron 
Creek lineage, and one population (Dude Creek), which is considered a 
mixed-lineage population (i.e., a stream or metapopulation that 
contains multiple lineages of Gila trout, instead of a single lineage). 
Recently, the Spruce Creek and Whiskey Creek lineages each lost a 
population following large-scale, high-severity wildfires in 2011 and 
2012, respectively.
    For Gila trout to be able to sustain populations in the wild over 
time (viability), the species requires combinations of sufficiently 
large, healthy populations that, where possible, have connectivity to 
dendritic stream networks to maintain adequate population sizes and 
genetic variation. Dendritic stream networks provide Gila trout with 
access to suitable habitat enabling the species to respond to changes 
in their biological and physical environment (representation), 
environmental stochasticity (resiliency), and catastrophic events 
(redundancy). Few, if any, extant populations of Gila trout are large 
enough to survive extremes in environmental conditions, and the 
existing genetic diversity of the species is limited to five remnant 
lineages. Recovery actions implemented to date have increased the 
number of populations of Gila trout; however, the spatial distribution 
of populations is constrained by the patchy distribution and geographic 
isolation of cold-water streams, many of which are single-stream 
systems that are relatively small. Significant factors affecting the 
viability of Gila trout include habitat loss and fragmentation (Factor 
A) that result from large-scale, high-severity wildfire and the effects 
of climate change; unregulated angling (Factor B); predation and 
competition from nonnative fish that are naturalized throughout the 
Gila trout's historical range (Factor C); and hybridization with 
rainbow trout (Oncorhynchus mykiss) and small, isolated population 
sizes (Factor E).

Recovery Plan Goals

    The objective of a recovery plan is to provide a framework for the 
recovery of a species so that protection under the ESA is no longer 
necessary. A recovery plan includes scientific information about the 
species and provides criteria and actions necessary for us to be able 
to reclassify the species to threatened status or remove it from the 
lists of endangered and threatened wildlife and plants. Recovery plans 
help guide our recovery efforts by describing actions we consider 
necessary for the species' conservation, and by estimating time and 
costs for implementing needed recovery measures.
    In this revised recovery plan, we transition from a strategy of 
crisis-management focused on preventing extinction to an approach of 
establishing sustainable populations throughout the historical range of 
the Gila trout, populations that contain the breadth of genetic 
diversity of the species. The recovery strategy for the Gila trout will 
entail incremental replacement of nonnative salmonids with Gila trout 
in suitable habitat throughout a significant portion of the historical 
range of the species. This strategy will be implemented by conducting 
actions to substantially improve redundancy, representation, and 
resiliency to the point that the species is no longer at risk for 
extinction and may be delisted. Recovery objectives include securing 
the existing genetic diversity of Gila trout, increasing the geographic 
distribution of the species, and increasing the size, dendritic 
population structure, and interconnectedness of populations. The 
revised recovery plan provides recovery criteria aimed at managing or 
eliminating threats to meet the goal of delisting the species. These 
recovery criteria are based on the area of occupied habitat within the 
Gila trout's presumed historical range, the conservation of genetically 
distinct Gila trout lineages, the establishment of dendritic 
metapopulations, and the absence and management of nonnative salmonids 
within Gila trout habitat. The site-specific management actions needed 
to address the threats to Gila trout viability and achieve the recovery 
criteria involve: (1) Repatriation of Gila trout to streams within its 
presumed historical range; (2) establishment and maintenance of captive 
propagation and hatchery facilities; (3) management of nonnative 
salmonids; (4) monitoring of Gila trout populations; (5) conducting 
public education and outreach; and (6) developing and implementing 
regulations to maintain sustainable Gila trout populations in streams 
open to sport fishing.

Request for Public Comments

    Section 4(f) of the ESA requires us to provide public notice and an 
opportunity for public review and comment during recovery plan 
development. It is also our policy to request peer review of recovery 
plans (July 1, 1994; 59 FR 34270). In an appendix to the approved 
recovery plan, we will summarize and respond to the issues raised by 
the public and peer reviewers. Substantive comments may or may not 
result in changes to the recovery plan; comments regarding recovery 
plan implementation will be forwarded as appropriate to Federal or 
other entities so that they can be taken into account during the course 
of implementing recovery actions. Responses to individual commenters

[[Page 36572]]

will not be provided, but we will provide a summary of how we addressed 
substantive comments in an appendix to the approved recovery plan.
    We invite written comments on the draft recovery plan. In 
particular, we are interested in additional information regarding the 
current threats to the species and the implementation of the 
recommended recovery actions.

Public Availability of Comments

    All comments received, including names and addresses, will become 
part of the administrative record and will be available to the public. 
Before including your address, phone number, email address, or other 
personal identifying information in your comment, you should be aware 
that your entire comment--including your personal identifying 
information--may be made publicly available. If you submit a hardcopy 
comment 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.

Authority

    We developed our draft recovery plan and publish this notice under 
the authority of section 4(f) of the Endangered Species Act of 1973, as 
amended (16 U.S.C. 1531 et seq.).

Amy L. Lueders,
Regional Director, Southwest Region, U.S. Fish and Wildlife Service.
[FR Doc. 2021-14733 Filed 7-9-21; 8:45 am]
BILLING CODE 4333-55-P


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