[Federal Register Volume 83, Number 2 (Wednesday, January 3, 2018)]
[Proposed Rules]
[Pages 330-341]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2017-28313]


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DEPARTMENT OF THE INTERIOR

Fish and Wildlife Service

50 CFR Part 17

[Docket No. FWS-R4-ES-2017-0061; 4500030113]
RIN 1018-BC14


Endangered and Threatened Wildlife and Plants; Threatened Species 
Status for the Panama City Crayfish

AGENCY: Fish and Wildlife Service, Interior.

ACTION: Proposed rule.

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SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a 
12-month finding on a petition to list the Panama City crayfish 
(Procambarus econfinae), a semi-terrestrial crayfish species native to 
Bay County, Florida, as a threatened species under the Endangered 
Species Act (Act). After review of the best available scientific and 
commercial information, we find that listing this species is warranted. 
Accordingly, we propose to list the Panama City crayfish as a 
threatened species under the Act. If we finalize this rule as proposed, 
it would extend the Act's protections to this species and add this 
species to the Federal List of Endangered and Threatened Wildlife 
(List).

DATES: We will accept comments received or postmarked on or before 
March 5, 2018. Comments submitted electronically using the Federal 
eRulemaking Portal (see ADDRESSES, 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 February 20, 2018.

ADDRESSES: Document availability: The report upon which this proposed 
rule is based (see SUPPLEMENTARY INFORMATION) is available at http://www.regulations.gov in Docket No. FWS-R4-ES-2017-0061 and on the 
Service's Southeast Region website at https://www.fws.gov/southeast/.
    Comment submission: You may submit comments by one of the following 
methods:
    (1) Electronically: Go to the Federal eRulemaking Portal: http://www.regulations.gov. In the Search box, enter FWS-R4-ES-2017-0061, 
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-R4-ES-2017-0061; U.S. Fish and Wildlife 
Service, MS: BPHC, 5275 Leesburg Pike, Falls Church, VA 22041-3803.
    We request that you send comments only by the methods described 
above. We will post all comments on http://www.regulations.gov. This 
generally means that we will post any personal information you provide 
us (see Public Comments, below, for more information).

FOR FURTHER INFORMATION CONTACT: Catherine Phillips, Field Supervisor, 
U.S. Fish and Wildlife Service, Panama City Ecological Services Field 
Office, 1601 Balboa Avenue, Panama City, FL 32405; telephone 850-769-
0552; facsimile 850-763-2177. Persons who use a telecommunications 
device for the deaf (TDD) may call the Federal Relay Service at 800-
877-8339.

SUPPLEMENTARY INFORMATION: 

Executive Summary

    Why we need to publish a rule. Under the Act, if we determine that 
a species is 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 be completed only by issuing a rule.
    This rule proposes adding the Panama City crayfish (Procambarus 
econfinae) as a threatened species to the List of Endangered and 
Threatened Wildlife in title 50 of the Code of Federal Regulations (50 
CFR 17.11(h)).
    The basis for our action. Under the Act, we may determine that a 
species is an endangered or threatened species 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 habitat loss and 
fragmentation from development (Factor A) is the primary threat to the 
Panama City crayfish.

Supporting Documents

    A species status assessment (SSA) team prepared an SSA report for 
the Panama City crayfish. The SSA team was composed of Service 
biologists, in consultation with other species experts. The SSA report 
represents a compilation of the best scientific and commercial data 
available concerning the status of the species, including the impacts 
of past, present, and future factors (both negative and beneficial) 
affecting the species. Maps depicting the historical range and current 
populations are included in the SSA for reference.
    Peer review. We solicited independent peer review of the SSA Report 
by six individuals with expertise in crayfish; aquatic invertebrates, 
population, or landscape ecology; genetics and conservation genetics; 
and/or speciation and conservation biology. We received comments from 
one of the six peer reviewers. The SSA report and other materials 
relating to this proposal can be found on the Service's Southeast 
Region website at https://www.fws.gov/southeast/ and at http://www.regulations.gov under Docket No. FWS-R4-ES-2017-0061.

[[Page 331]]

Information Requested

Public Comments

    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 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 Panama City crayfish's biology, range, and population 
trends, including:
    (a) Biological or ecological requirements of the species, including 
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) Factors that may affect the continued existence of the species, 
which may include habitat modification or destruction, overutilization, 
disease, predation, the inadequacy of existing regulatory mechanisms, 
or other natural or manmade factors.
    (3) Biological, commercial trade, or other relevant data concerning 
any threats (or lack thereof) to this species and existing regulations 
that may be addressing those threats.
    (4) Additional information concerning the historical and current 
status, range, distribution, and population size of this species, 
including the locations of any additional populations of this species.
    (5) Specific prohibitions and exceptions to those prohibitions that 
may be necessary and advisable for the Panama City crayfish's 
conservation. We intend to publish, as appropriate, a more tailored 
proposed rule with provisions set forth under section 4(d) of the Act 
for public review and comment in the future. Activities we are 
considering for potential exemption under a section 4(d) rule include, 
but are not necessarily limited to, exceptions for:
    (a) Specific soil and vegetation restoration activities that will 
benefit the Panama City crayfish;
    (b) Water quality improvement;
    (c) Genetic and population monitoring;
    (e) Activities that maintain native vegetation near occupied or 
likely to be occupied Panama City crayfish habitat;
    (f) Sustainable silviculture practices that primarily occur 
adjacent to Panama City crayfish habitat and that are implemented 
according to certified best management practices; or
    (g) Any additional activities that should fall under the 4(d) rule.
    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 an endangered or threatened 
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 ADDRESSES. We request that you 
send comments only by the methods described in ADDRESSES.
    If you submit information via http://www.regulations.gov, your 
entire submission--including any personal identifying information--will 
be posted on the website. 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 http://www.regulations.gov.
    Comments and materials we receive, as well as supporting 
documentation we used in preparing this proposed rule, will be 
available for public inspection on http://www.regulations.gov, or by 
appointment, during normal business hours, at the U.S. Fish and 
Wildlife Service, Panama City Ecological Services Field Office (see FOR 
FURTHER INFORMATION CONTACT).

Public Hearing

    Section 4(b)(5) of the Act provides for one or more public hearings 
on this proposal, if requested. Requests must be received by the date 
listed above in DATES. Such requests must be sent to the address shown 
in FOR FURTHER INFORMATION CONTACT. 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.

Peer Review

    In accordance with our joint policy on peer review published in the 
Federal Register on July 1, 1994 (59 FR 34270), and our August 22, 
2016, memorandum updating and clarifying the role of peer review of 
listing actions under the Act, we sought the expert opinions of six 
appropriate specialists regarding the SSA report, which informed this 
proposed rule. We received a response from one of the six peer 
reviewers. The purpose of peer review is to ensure that our listing 
determination is based on scientifically sound data, assumptions, and 
analyses. The peer reviewers have expertise in crayfish biology, 
habitat, and stressors to the species. We invite any additional comment 
from the peer reviewers during this public comment period; these 
comments will be available along with other public comments in the 
docket for this proposed rule.

Previous Federal Action

    In 2010, the Center for Biological Diversity (CBD) petitioned the 
Service to list 404 aquatic, riparian, and wetland species from the 
Southeastern United States under the Act. The Panama City crayfish was 
among these 404 species. On September 27, 2011, the Service published a 
substantial 90-day finding for 374 of the 404 species, including the 
Panama City crayfish, soliciting information about, and initiating 
status reviews for, those species (76 FR 59836). In 2015, CBD filed a 
complaint against the Service for failure to complete a 12-month 
finding for the Panama City crayfish within the statutory timeframe. 
The Service entered into a settlement agreement with CBD to address the 
complaint; the court-approved settlement agreement specified that a 12-
month finding for the Panama City crayfish would be delivered to the 
Federal Register by September 30, 2017. On September 21, 2017, the 
Court approved an extension, allowing the Service to submit this 12-
month finding to the Federal Register no later than December 29, 2017.

Background

    A thorough review of the taxonomy, life history, and ecology of the 
Panama City crayfish (Procambarus econfinae) is presented in the SSA 
report, version 1.0 (Service 2017). The SSA report documents the 
results of our comprehensive biological status review for the Panama 
City crayfish, including an assessment of the potential stressors

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to the species. The SSA report does not represent a regulatory decision 
by the Service on whether the species should be proposed for listing as 
an endangered or threatened species under the Act. It does provide the 
scientific basis that informs that decision, which involves the further 
application of standards within the Act and its implementing 
regulations and policies. The full SSA report can be found on the 
Service's Southeast Region website at https://www.fws.gov/southeast/ 
and at http://www.regulations.gov under Docket No. FWS-R4-ES-2017-0061.

Species Description

    The Panama City crayfish is a small, semi-terrestrial crayfish that 
grows to about 2 inches (in) (50.8 millimeters (mm)) in length (minus 
claws), and is found in south-central Bay County, Florida. The species' 
color pattern consists of a medium dark-brown background color, lighter 
brown mid-dorsal stripe, and darker brown dorsolateral stripes (FWC 
2016, p.1). The Panama City crayfish was first described by Hobbs in 
1942 from Bay County, Panama City, Florida. Currently, the Panama City 
crayfish is classified in the family Cambaridae and is considered a 
valid taxon by the scientific community (Taylor et al. 1996, 2007; 
Integrated Taxonomic Information System 2017). The life history of the 
Panama City crayfish specifically is not well known. Cambarid crayfish 
may live about 2.5 to 3 years (Hobbs 2001, p. 977), with a generation 
period of 2 years. For this family of crayfish, the majority breed more 
than once, with mating among mature yearlings frequent; however, many 
individuals do not become sexually active until late summer or fall. 
Females may produce between 30 and 160 eggs, and have been found with 
eggs and/or young from March through September. Juveniles are most 
frequently found in the summer and have been observed through December, 
so young appear to be produced from at least March through December. 
Juveniles can be carried overland by sheet flow during rainy periods, 
which aids in dispersal (Keppner and Keppner 2002, p. 11).
    Eight crayfish species are known to occur within the range of the 
Panama City crayfish, although only the hatchet crayfish, Procambarus 
kilbyi, and the jackknife crayfish, Procambarus hubbelli, are found in 
the same habitat as the Panama City crayfish and may co-occur with it 
(FWC 2017). The Panama City crayfish is not known to hybridize with 
other species of crayfish.
    Historically, the species inhabited natural and often temporary 
bodies of shallow fresh water within open pine flatwoods and wet 
prairie-marsh communities. However, most of these communities have been 
cleared for residential or commercial development or replaced with 
slash pine plantations. The Panama City crayfish currently is known to 
inhabit the waters of grassy, gently sloped ditches and swales, slash 
pine plantations, utility rights-of-way and a few remnant parcels 
protected under wetland and private easements (FWC 2016, p. 2).
    The highest densities of Panama City crayfish have been recorded in 
areas with little to no shrub or tree cover (FWC 2016, p.2). Suitable 
habitat is normally dominated by herbaceous vegetation. Lowest 
population densities have occurred in small, open sites where shrubs or 
trees were present, or in the furrows between bedding rows in some pine 
plantations (Keppner and Keppner 2005). When encountered in dense titi 
(Cyrilla racemiflora and Cliftonia monophylla) swamps, the species was 
associated with temporarily inundated areas open to the sun with some 
herbaceous vegetation. Such sites may be considered secondary or 
suboptimal habitat for the species. On sites where mixed habitat 
features are present (e.g., partially wooded sites or sites with 
permanent, deep-water ponds), the Panama City crayfish appears to 
select favorable areas dominated by herbaceous vegetation, with shallow 
or fluctuating water levels (FWC 2016, p. 3; Keppner and Keppner 2005).
    The Panama City crayfish relies on particular soil types for burrow 
construction and supporting the herbaceous vegetation; these soil types 
are categorized as core or secondary soils. Core soils provide the best 
substrate to support the species; secondary soils are less ideal but 
still used. The core and secondary soil types that support Panama City 
crayfish within their known range are described in more detail in the 
SSA report (Service 2017, pp. 23-24).
    Panama City crayfish build burrows for shelter and are categorized 
as secondary burrowers, which are normally in surface water when it is 
present on the hydric soils they inhabit (Hobbs 1981). They construct 
burrows that contact the water table as the surface water of their 
habitat recedes, and they occupy burrows when surface water is absent 
or during periods of extreme water temperatures. They emerge from the 
burrows when surface water is present again or water temperatures are 
favorable. It appears that they can survive significant periods of 
drought in their burrows when they can maintain contact with the water 
table. During these dry periods the Panama City crayfish excavates and 
lives in unbranched burrows up to three feet long that extend down to 
the water table, thereby enabling the species to remain adequately 
hydrated and survive (FWC 2016, p. 3).
    Little is known about the specific feeding habits of the Panama 
City crayfish. Observations on Panama City crayfish that were held in 
aquaria spanning 1.5 plus years (Keppner 2014) indicate that they are 
detritivores and herbivores. Specimens were offered dead animal 
material, but they avoided it in favor of processing the substrate for 
particles of prepared fish food and the fresh aquatic vegetation that 
were provided as primary food sources. Herbaceous vegetation likely 
serves as a food source for the Panama City crayfish.
    The Panama City crayfish historically ranged throughout south-
central Bay County, Florida within a 56 square mile area (see Figure 
1). The historical range likely created one population connected by 
core and secondary soils. As urban growth came to Panama City, the 
range became fragmented and isolated patches. Today, the species has 13 
localized populations that can be divided into two distinct groups: The 
western and eastern group. The western group includes 8 separate 
populations and the eastern group includes 5 separate populations. The 
13 populations are described in more detail in the SSA report (Service 
2017, pp. 35-54).

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[GRAPHIC] [TIFF OMITTED] TP03JA18.009

Species Needs and Viability

    The Panama City crayfish needs freshwater wetlands that support 
herbaceous vegetation, which is important to the Panama City crayfish 
for food, shelter, and detritus formation. The species needs core or 
secondary soils to provide the proper sediment structure for burrow 
construction and to support the herbaceous vegetation. The Panama City 
crayfish needs access to groundwater (through burrowing) or surface 
water to prevent desiccation of individuals and populations. The 
species needs both adequate water quality and quantity to fulfill its 
life history.
    We describe the Panama City crayfish's viability by characterizing 
the status of the species in terms of its resiliency (ability of the 
populations to withstand stochastic events), redundancy (ability of the 
species to withstand large-scale, catastrophic events), and 
representation (the ability of the species to adapt to changing 
environmental conditions). Using various time frames and the current 
and projected resiliency, redundancy, and representation, we describe 
the species' level of viability over time. For the Panama City crayfish 
to maintain viability, its populations or some portion thereof must be 
resilient. A number of factors influence the resiliency of Panama City 
crayfish

[[Page 334]]

populations, including the inbreeding coefficient, population 
isolation, and population abundance. Elements of Panama City crayfish 
habitat that determine whether Panama City crayfish populations can 
grow to maximize habitat occupancy influence those factors, thereby 
increasing the resiliency of populations. These demographic and habitat 
factors are discussed here; for each factor, we assigned a condition 
category of high, medium, or low (see Table 1). We evaluated each 
population and assigned it a high, medium, or low condition category 
for each factor, as well as an overall condition.

                                            Table 1--Demographic and Habitat Factors for Panama City Crayfish
                                                                  [Service 2017, p. 64]
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                                             Demographic factors                                            Habitat elements
                              --------------------------------------------------------------------------------------------------------------------------
     Condition  category                         Population                                                                                  Suitable
                                 Inbreeding       isolation      Population        Freshwater quality &        Herbaceous ground cover        habitat
                                 coefficient        (km)          abundance              quantity                                             (acres)
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High.........................          >0.400            <0.5             >51  <33% developed and            easements or ROW with >15              >800
                                                                                unsuitable.                   acres that is managed.
Moderate.....................     0.200-0.400         0.5-2.0           21-50  33-66% developed and          easements or ROW with <=15          100-800
                                                                                unsuitable.                   acres suitable habitat
                                                                                                              that is managed; or timber
                                                                                                              lands.
Low..........................          <0.200              >2            1-20  >66% developed and            no managed lands, habitat              <100
                                                                                unsuitable acres.             currently a titi
                                                                                                              monoculture.
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Population Isolation: Least-cost path distance to nearest population in kilometers.
Population Abundance: Based on population sampling counts from all conducted surveys recorded.
Freshwater Quality & Quantity: Percentage of developed and unsuitable acres within the area supporting each population.
Herbaceous Ground Cover: Includes land with and without easements, size of easements, and management activities.
Suitable Habitat: Acres of undeveloped core and secondary soils within the area supporting each population.

    Inbreeding coefficient: The Panama City crayfish, once connected 
through core and secondary soils within a 56 square mile area, is now 
separated into 13 populations that, when combined, total a 
significantly smaller area than occupied by the historical, 
interconnected population. A recent genetic analysis of population 
differentiation and clustering to assess population structure of the 
Panama City crayfish quantified each population's inbreeding 
coefficient numbers (Duncan et al. 2017). An inbreeding coefficient 
number shows the probability of inheriting two copies of the same 
allele from an ancestor that occurs on both sides of the pedigree. For 
Panama City crayfish populations, the differences in inbreeding 
coefficient numbers likely correspond to patterns of fragmentation from 
urban development and not necessarily from selective pressures 
maintaining adaptive differences. Little work has been done on the 
population genetics of wild crayfish populations. We have no comparison 
for values in crayfish species of expected inbreeding coefficients 
(Duncan et al. 2017), and treat this as a relative measure. Thus, we 
ranked individual populations into three numerically distinct breaks: 
Low when inbreeding coefficients were less than 0.200, moderate when 
they ranked between 0.200-0.400, and high when results were greater 
than 0.400.
    Population isolation: To promote genetic connectivity in Panama 
City crayfish, we must have an understanding of their potential 
abilities to move between populations. One working hypothesis was that 
ditches within the range promote movement, especially during flooding 
events. This idea is supported by observations of some localized 
movements of Panama City crayfish into previously unoccupied ditches 
after recent flooding where they were not seen in these new locations 
during the next sampling event.
    Because the landscape occupied by the Panama City crayfish is 
spatially heterogeneous, it is important to understand how certain 
landscape features affect the species' ability to move in order to meet 
requirements for foraging, migration, or other movement-dependent 
processes (Crooks and Sanjayan 2006 as cited in Duncan et al. 2017). We 
relied on a landscape ``Least Cost Path'' land cover analysis conducted 
by Duncan et al. (2017) to assist in determining what may affect 
genetic connectivity in Panama City crayfish and inform our 
understanding of population isolation.
    Population abundance: The size of an individual population coupled 
with age and sex classifications can be used as an indicator of 
resiliency. Within the SSA report, we have summarized the years that 
surveys of varying levels were completed within each population. The 
protocol currently used for PCC monitoring typically depends on dip-net 
sampling when sufficient surface water is present and nondestructive 
evaluation of crayfish burrows. The protocol can miss specimens in 
vegetation and does not sample individuals living below ground in 
burrows, and we currently do not have an estimate of detection 
probability using this protocol. The protocol is quantitative and 
results in a catch per standard unit effort estimate of the population. 
We use population counts to assess the relative population size across 
the range of the species.
    Freshwater quality and quantity: Although crayfish are facultative 
air breathers, moisture is required to facilitate the respiratory 
process (Longshaw and Stebbing 2016, p. 327). Burrowing to groundwater 
or access to surface water are both important habitat features needed 
to prevent desiccation of individuals and populations. Declines in 
water quality are known to present a significant threat to other 
species of crayfish (and presumably to PCC). These declines can range 
from oxygen-deficient conditions resulting from algal blooms, sewage 
spills, or localized leaks to pollution originating from roadway runoff 
or chemical spills (Acosta and Perry 2001). The Panama City crayfish 
often inhabits ditches and swales close or adjacent to commercial and 
private properties, which may affect the water quality at these sites. 
We used a proxy measure of water quality and quantity based on the 
amount of development surrounding the population. We assumed that 
greater acreage in developed and unsuitable landcover types (which 
includes transportation and other development-related types) is 
correlated with declines in this habitat element. Herbaceous ground 
cover: Herbaceous vegetation is important to the Panama City crayfish

[[Page 335]]

for food, detritus formation, and cover. Absence of vegetation 
increases exposure of this small crayfish to predation and reduces 
availability of food. Suitable habitat: Species sampling efforts and a 
recent landscape modeling analysis support the theory that the Panama 
City crayfish almost exclusively relies on core and secondary soils. 
These soils provide the sediment structure needed for burrow 
construction to the water table and also support the herbaceous 
vegetation upon which the species relies for food and cover. Lands 
supporting the Panama City crayfish must be of sufficient size to 
sustain a population, but we don't know the minimum size, as many 
factors influence a Panama City crayfish population, including other 
habitat conditions. The recent work of Duncan et al. (2017) showed that 
all remaining populations with >800 acres of suitable habitat 
supporting them were genetically healthy, and population counts support 
this as well.
    Maintaining representation in the form of genetic or ecological 
diversity is important to maintain the Panama City crayfish's capacity 
to adapt to future environmental changes. The 13 remaining populations 
show relatively high genetic differentiation with inbreeding 
coefficients ranging from 0.214 to 0.493 and associated acreages of 
suitable habitat ranging from 5 acres to 5,309 acres.
    Redundancy reduces the risk that a large portion of the species' 
range will be negatively affected by a natural or anthropogenic 
catastrophic event at a given point in time. Species that have 
resilient populations spread throughout their historical range are less 
susceptible to extinction (Carroll et al. 2010; Redford et al. 2011). 
The Panama City crayfish historically lacked redundancy in that its 
historical range consisted of one population of interconnected soils. 
Today, there is a distinct genetic difference between individual 
patches located in the western range versus individual patches within 
the eastern range, which likely corresponds to patterns of 
fragmentation from urban development as well as some natural wetland 
buffers (creeks, stream bodies) (Duncan et al. 2017).

Summary of Biological Status and Threats

    We completed a comprehensive assessment of the biological status of 
the Panama City crayfish, and prepared a report of the assessment, 
which provides a thorough account of the species' overall viability. In 
this section, we summarize the conclusions of that assessment, which 
can be accessed at Docket No. FWS-R4-ES-2017-0061 on http://www.regulations.gov.

Summary of Factors Affecting the Species

    The Act directs us to determine whether any species is an 
endangered species or a threatened species because of any factors 
affecting its continued existence. We reviewed the potential risk 
factors (i.e., threats, stressors) that could be affecting the Panama 
City crayfish now and in the future. In this proposed rule, we will 
discuss in detail only those factors that could meaningfully impact the 
status of the species. The primary risk factors (i.e., threats) 
affecting the status of the Panama City crayfish are habitat loss and 
degradation, habitat fragmentation, and subpopulation isolation due to 
development (Factor A from the Act). Additional stressors to the 
species include collection for bait (Factor B), disease (Factor C), 
off-road vehicle use (Factor A), and insecticide application (Factor 
E); however, our analysis shows that while these stressors may be 
impacting individual Panama City crayfish, they are not having species-
wide impacts. For a full description of all identified stressors, refer 
to chapter 4 of the SSA report (Service 2017).
Factor A. The Present or Threatened Destruction, Modification, or 
Curtailment of Its Habitat or Range
    Development projects and land conversion can result in direct loss 
of habitat, as well as fragmentation and isolation of populations. The 
effects of development may also include alterations to water quality 
and quantity. Historically, the Panama City crayfish inhabited natural 
and often temporary bodies of shallow fresh water within open pine 
flatwoods and wet prairie-marsh communities (Hobbs 1942). The Panama 
City crayfish's natural habitat (wet pine flatwoods) has been lost or 
degraded through residential, commercial, and industrial development, 
as well as conversion to intensive pine silviculture and for ranching 
and farming uses. It is likely that no unaltered natural pine flatwoods 
remain within the Panama City crayfish's current range.
    Most known Panama City crayfish occurrences are in human-altered 
habitats and are vulnerable to further loss or alteration. Although 
artificial habitats such as roadside ditches and rights-of-way have 
allowed the Panama City crayfish to persist in areas from which they 
would otherwise likely have been extirpated, human activities can alter 
the hydrology and configuration of these sites, making them unsuitable 
for long-term Panama City crayfish persistence. For example, roadside 
ditch maintenance and construction activities have resulted in the 
destruction of several crayfish sites.
    While ditch maintenance activities may have temporary negative 
impacts on the species, if conducted using conservation management 
principles, they may provide long-term habitat improvements that 
support Panama City crayfish presence. For example, the design of the 
ditch helps determine whether it can support Panama City crayfish. 
Swales and ditches with herbaceous vegetation and a 3:1 or shallower 
slope are more likely to support Panama City crayfish than ditches with 
a steeper slope (FWC 2017, p. 22).
    Infrastructure development has impacted, or is anticipated to 
impact, several crayfish sites (Keppner and Keppner 2001, pp. 13-14, 
2004, p. 9). For example, several proposed road construction or 
expansion projects, such as the widening of Star Avenue and Kern Avenue 
and the widening and hardening of Tram Road, may impact Panama City 
crayfish habitat in the future. Infrastructure development can 
eliminate suitable Panama City crayfish habitat by removing the 
required herbaceous vegetation and digging up the surrounding soils.
    Silvicultural practices such as ditching and bedding, roller 
chopping, installing fire breaks, and constructing roads can alter the 
hydrology of Panama City crayfish sites, create physical barriers to 
crayfish movement, and destroy underground burrows (Hobbs 2001, p. 988; 
Keppner and Keppner 2001, p. 13, 2004, p. 10; FWC 2006, p. 10). These 
activities may contribute to the isolation of Panama City crayfish 
populations. Fire suppression and high tree density on silvicultural 
sites can reduce herbaceous groundcover necessary for suitable crayfish 
habitat (Keppner and Keppner 2001, p. 13, 2004, p. 10; FWC 2006, p. 
27). Similarly, removal of tree canopy cover, changes in ground cover 
vegetation, and associated changes in water quality and surface water 
availability are all possible changes associated with the effects of 
conversion to farming and ranching practices, such as cattle grazing 
(e.g., Jansen and Robertson 2001, pp. 71-73). These activities 
negatively impact the habitat of the Panama City crayfish. Although 
minimal changes are expected to occur due to farming and ranching 
practices, conversion from silviculture to grazing use has occurred on 
lands adjacent the crayfish's range.

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    Freshwater crayfish may be sensitive to declines in water quality 
and declines have been identified as a threat to other crayfish 
species. Water quality declines can range from oxygen-deficient 
conditions resulting from algal blooms or sewage spills to pollution 
originating from roadway runoff, pesticide applications, or chemical 
spills (Acosta and Perry 2001, p. 46). Given the level of development 
throughout the range of the Panama City crayfish and the occurrences of 
Panama City crayfish adjacent to private properties, runoff from roads 
or improper application of chemicals, such as pesticides or 
fertilizers, may negatively impact water quality and have direct 
impacts on the species.
    The majority of known Panama City crayfish occurrences in the 
western part of the range are in roadside ditches and swales that are 
isolated from other Panama City crayfish populations by roads, 
development, and land use changes. Fragmentation and isolation can 
increase vulnerability to local extirpation due to adverse genetic, 
demographic, and environmental events. Further, when Panama City 
crayfish have been extirpated from an area, lack of habitat connections 
between sites can prevent Panama City crayfish from recolonizing the 
newly vacant sites (FWC 2006, p. 10). Recent genetic work indicates the 
isolation in the western portion of the range has resulted in 
inbreeding and drift (Duncan et al. 2017, p. 17).
    In addition to the effects on habitat described above, many of the 
activities contributing to habitat loss and degradation can also 
directly harm or kill Panama City crayfish. Continuous loss of 
individuals can eventually lead to extirpation of isolated populations. 
In particular, roadside maintenance, dredging, and infrastructure 
development in roadside ditches and silvicultural and farming 
activities, if done without appropriate safeguards, have the potential 
to kill, harm, or displace Panama City crayfish due to the removal by 
heavy machinery of soil from crayfish sites. In addition, fill placed 
on sites in preparation for construction activities can entomb crayfish 
in their burrows
    Off-road vehicle use may impact the Panama City crayfish by 
crushing, as well as impacting the habitat through rutting of the soil 
and destruction of vegetation (FWC 2016, p. 11). Off-road vehicle use 
has been documented in areas within the eastern part of the Panama City 
crayfish's range along Gulf Power rights-of-way. Gulf Power has blocked 
access to these rights-of-way with gates, so access to these areas is 
limited and we do not expect off-road vehicle use is resulting in 
species-wide impacts.
Factor B. Overutilization for Commercial, Recreational, Scientific, or 
Educational Purposes
    Crayfish may be recreationally harvested for fish bait. Within the 
range of the Panama City crayfish, several of the areas where the 
species occurs are known to be utilized by locals collecting fish bait 
(FWC 2016, p.11; Keppner and Keppner 2001, 2005). However, although 
harvesting individual crayfish at these sites has been documented, the 
actual species collected are unknown. Therefore, while harvesting 
crayfish may be impacting individual Panama City crayfish, we find that 
it is not having a species-wide impact.
    Florida State Code 68A-9.002 authorizes the Director of the Florida 
Fish and Wildlife Conservation Commission to issue permits to collect 
any wildlife species for ``scientific, educational, exhibition, 
propagation, management or other justifiable purposes.'' Permits have 
been issued for biologists conducting surveys on the Panama City 
crayfish; however, the Panama City crayfish is not known to be targeted 
for significant scientific or educational collections.
Factor C. Disease or Predation
    Disease agents and pests identified for freshwater crayfish include 
viruses, bacteria, rickettsia-like organisms, fungi, protistans, and 
metazoans (Evans et al. 2002, p. 1). There is no reported information 
on the presence of disease or parasites in the Panama City crayfish to 
date. Nothing indicates that predation or competition by native or non-
native predators is currently affecting Panama City crayfish at the 
species level.
Factor D. The Inadequacy of Existing Regulatory Mechanisms
    The following existing regulatory mechanisms were considered and 
discussed as they relate to the stressors, under the applicable 
Factors, affecting the Panama City crayfish: Florida State Code 68A-
9.002 (Factor B).
    The Panama City crayfish is currently identified as a State Species 
of Special Concern in Florida (Florida State Code 68A-27.005). Species 
of Special Concern require individuals to obtain a permit from the FWC 
Executive Director in order to take, possess, transport, or sell the 
species.
    FWC has developed voluntary draft guidelines for developers to 
consider when undertaking projects that may impact Panama City crayfish 
and its habitat (FWC 2016). However, these guidelines are not 
regulatory in nature. We are not aware of any regulatory mechanisms in 
place to address the threat of habitat loss, fragmentation, and 
degradation due to development.
Factor E. Other Natural or Manmade Factors Affecting Its Continued 
Existence
    The Service considered several additional stressors to the Panama 
City crayfish, including chemical application and sea level rise.
    Mosquitocides are used within the range of the Panama City crayfish 
to treat both larval and adult mosquitoes. The mosquitocides registered 
for use within the range of the Panama City crayfish do not pose known 
threats to water quality if applied per label directions (FWC 2016, p. 
10). Fertilizers, insecticides, and herbicides may pose a risk to 
Panama City crayfish if applied inappropriately.
    The Panama City crayfish was included in a statewide vulnerability 
assessment for approximately 1000 species in Florida (Reece et al. 
2013, Hocter et al. 2014) using a Standardized Index of Vulnerability 
and Value Assessment (SIVVA; Reece and Noss 2014). Based on the data 
used in this assessment, the Panama City crayfish did not meet the 
vulnerability assessment criteria. The assessment used a 10 meter 
digital elevation model ``bathtub'' projection that showed 2 meters of 
sea level rise and overlapped these projections with species' `element 
occurrences.' (Reece et al 2013). The assessment focused on those 
species which had 50% or more of their occurrences intersecting with 
the sea level rise projection. The Panama City crayfish did not meet 
this criteria. Overall, little suitable habitat for Panama City 
crayfish will be affected by sea level rise (Hocter et al. 2014).

Conservation Actions

    Several private lands within the Panama City crayfish's range are 
being managed under conservation easements for the species. These 
easements largely cover wet pine flatwoods and wet prairie habitats. 
Other private lands are inaccessible to surveyors, but if they lack 
significant disturbance and have suitable habitat for the species, they 
are likely occupied by Panama City crayfish.
    Areas in silviculture adjacent to human-altered habitats may serve 
as refuges for Panama City crayfish, and silvicultural BMPs require 
operators to minimize impacts to Panama City crayfish. Use of BMPs for 
agriculture and grazing can also help minimize impacts to aquatic 
species (e.g., Florida

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Department of Agriculture and Consumer Services 2008, p. 1). Gulf Power 
Company manages rights-of-way along approximately 114 acres of land 
that is populated by the Panama City crayfish. The Service and FWC have 
a management agreement that provides recommended BMPs to Gulf Power 
Company; the management practices through this agreement have proven 
effective as the crayfish continue to thrive within the easement areas.

Current Condition

    The historical range of the Panama City crayfish included a 56-
square-mile area in Bay County, Florida. It was likely one contiguous 
population within open pine flatwoods and prairie-marsh communities 
providing connectivity across the landscape. Currently, the species is 
found in 13 genetically distinct populations within the boundaries of 
its historical range. Within its range, 61 percent (9,180 acres) of 
habitat with core soils and 46 percent (5,646 acres) of habitat with 
secondary soils remain undeveloped, and the total amount of available 
suitable habitat based on soils is 54 percent of the historical habitat 
available to the species.
    The current condition is a qualitative estimate based on an 
analysis of the three population factors (inbreeding, population 
isolation, and population sampling/relative abundance) and three 
habitat elements (water quality/availability, herbaceous ground cover, 
and suitable habitat). Overall population and habitat condition 
rankings were determined by combining the three population factors and 
three habitat elements using the most frequent score for individual 
factors as the overall score. Of the 13 populations described, the 
current conditions show 4 (31 percent) populations are estimated to 
have high resiliency, 5 (38 percent) moderate resiliency, and 4 (31 
percent) low resiliency. In the western group of populations, 4 
populations have low resiliency, 3 populations have moderate 
resiliency, and 1 has high resiliency. In the eastern group, 2 
populations have moderate resiliency and 3 populations have high 
resiliency. Generally, genetic variation is low and inbreeding is high 
across the range, which indicate a high degree of current population 
isolation. This pattern is generally more pronounced in the sampling 
locations in the west (heavily urbanized areas).

Future Condition

    For the purpose of this assessment, we define viability as the 
ability of the species to sustain populations in the wild over time. 
This discussion explains how the stressors associated with habitat 
loss, fragmentation, and degradation from residential and commercial 
development will influence resiliency, redundancy, and representation 
for the Panama City crayfish throughout its current known range using a 
series of plausible scenarios for 2030, 2050, and 2070. We predicted 
both future population factors (inbreeding and population isolation) 
and habitat factors (water quality and quantity, herbaceous ground 
cover, and suitable habitat) and evaluated these to inform our future 
conditions.
    To predict potential future changes related to urban growth, we 
used layers from the Southeast Regional Assessment Project (SERAP, from 
the Biodiversity and Spatial Analysis Center at North Carolina State 
University; 60m resolution), a modification of the SLEUTH Projected 
Urban Growth model (Jantz et al. 2010, entire; Terando et al. 2014, 
entire). SERAP identifies the parameters in global and regional models 
that are most likely to affect the Southeast region's climate and local 
landscape dynamics, with the goal of providing decision makers with 
information about low-probability, high-impact climate extremes through 
downscaled models and threats analysis. We used these products to map 
future predicted changes in urbanization in 2030, 2050, and 2070. The 
uncertainty associated with the SLEUTH model increases in time, as the 
species' response to the dynamic nature of the variables becomes less 
predictive. There is a greater confidence in predicting potential 
development and the species' response to changes in the landscape in 
the near future rather than the distant future.
    To address uncertainty associated with the degree and extent of 
potential future stressors and their impacts on species' requisites, 
the 3Rs were assessed using three scenarios: status quo development 
(i.e., >=80 percent probability of occurring), moderate development 
(>=30 percent probability of occurring), and high development (>=0 
percent probability of occurring). The scenarios included projecting 
possible future development using the SERAP model (Jantz et al. 2010, 
entire; Terando et al. 2014, entire). They also describe the predicted 
effects of the development on loss and fragmentation of suitable 
habitat rangewide and on each of 11 known populations, and draw 
inferences about population health based on the work of Duncan et al. 
(2017, entire). We excluded two populations (College Point and City of 
Lynn Haven) from our scenario analysis due to insufficient available 
data. Please refer to the SSA report (Service 2017) for the full 
analysis of the future scenarios.
    In scenario one, the ``status quo'' scenario, we considered the 
development most likely to occur. Based on the SERAP model, this was 
development with a <ls-thn-eq>=80 percent probability. Under this 
scenario, Panama City crayfish will lose 1,401 to 3,096 acres of 
habitat rangewide as developed land increases from 20,221 to 25,040 
acres. This loss, fragmentation, and degradation of habitat would 
reduce the number of resilient populations in high or moderate 
condition from nine currently to five by 2050. This loss of resiliency 
comes from both a reduction in habitat elements as well as the effects 
of isolation and drift on the populations themselves.
    Under the ``status quo'' scenario, only one resilient population 
(the St. Joe population) is predicted to remain in the western group by 
2050. This results in a loss of redundancy and representation, as only 
one resilient population will remain in the western group. In the 
eastern group, four resilient populations are predicted to persist 
through 2070.
    In scenario two, the ``intermediate development'' scenario, we 
considered development with a moderate potential to occur. Based on the 
SERAP model, this was development with a >=30 percent probability of 
occurring. In this scenario, the Panama City crayfish will lose 2,252 
to 4,854 acres of habitat rangewide as developed land increases from 
20,221 to 27,332 acres. This loss, fragmentation, and degradation of 
habitat is predicted to reduce the number of resilient populations in 
high or moderate condition from nine currently to four by 2070. This 
loss of resiliency comes from both a reduction in habitat elements as 
well as the effects of isolation and drift on the populations 
themselves.
    Under the ``intermediate development'' scenario, only one resilient 
population (the St. Joe population) is predicted to remain in the 
western group by 2050. This results in a loss of redundancy and 
representation, as only one resilient population will remain in the 
western group. In the eastern group, three resilient populations are 
predicted to persist through 2070.
    In scenario three, ``high development'' or ``worst case'' scenario, 
we considered the development that is least likely to occur. Based on 
the SERAP model, this was development with at >0 percent probability of 
occurring. In this scenario, the Panama City crayfish will lose 3,233 
to 6,130 acres of habitat

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rangewide as developed land increases from 20,221 to 28,899 acres. This 
loss, fragmentation, and degradation of habitat is predicted to reduce 
the number of resilient populations in high or moderate condition from 
nine currently to three by 2070. This loss of resiliency comes from 
both a reduction in habitat elements as well as the effects of 
isolation and drift on the populations themselves.
    Under the ``high development'' scenario, all resilient populations 
in the western group are predicted to be lost by 2050, resulting in a 
loss of all representation and redundancy in the western group. In the 
eastern group, three resilient populations are predicted to persist 
through 2070.

Determination

    Section 4 of the Act (16 U.S.C. 1533), and its implementing 
regulations at 50 CFR part 424, set forth the procedures for adding 
species to the Federal Lists of Endangered and Threatened Wildlife and 
Plants. Under section 4(a)(1) of the Act, we may list a species based 
on: (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 carefully assessed the best scientific and commercial 
information available regarding the past, present, and future threats 
to the Panama City crayfish. Our analysis of this information indicates 
that, at the species level, habitat development (Factor A) is the 
primary factor affecting the Panama City crayfish now and into the 
future. There may be additional infrastructure projects (e.g. roads, 
ditches, etc.) that affect the hydrology within the range of the Panama 
City crayfish as a result of forest clearing for permanent rights of 
way or silviculture. Additionally, the current level of habitat 
fragmentation (Factor A) further isolates populations, which reduces 
gene flow and limits the potential for the species to disperse. In 
addition, we have no evidence that ORV use (Factor A), overutilization 
(Factor B) or disease (Factor C) is affecting populations of Panama 
City crayfish.
    The Act defines an endangered species as any species that is ``in 
danger of extinction throughout all or a significant portion of its 
range.'' We find that an endangered species status is not appropriate 
for the Panama City crayfish because the species maintains multiple 
resilient populations across its historical range and the risk is low 
that the species would not persist in the near term; in other words, 
the risk of the Panama City crayfish significantly declining in the 
near term is low given that it has persisted despite historical levels 
of habitat loss. The current conditions as assessed in the Panama City 
crayfish SSA report show that only 43 to 54 percent of the original 
lands historically available to the Panama City crayfish remain 
potentially available for use by the Panama City crayfish. However, 
while the species' habitat has been reduced by at least 46 percent, the 
species currently consists of 13 populations, 9 of which are highly to 
moderately resilient and found across its historical range. Further, 
despite changes to the crayfish's natural habitat of wet pine 
flatwoods, the species currently persists using artificial habitats 
such as roadside ditches and rights-of-way although these sites may 
become unsuitable long term due to anthropogenic activities that can 
alter their hydrology or configuration. Therefore, we conclude that the 
current risk of extinction of the Panama City crayfish is sufficiently 
low that it does not meet the definition of an endangered species under 
the Act.
    The Act defines a threatened species as any species that is 
``likely to become endangered throughout all or a significant portion 
of its range within the foreseeable future.'' We find that the status 
of the Panama City crayfish meets the definition of a threatened 
species. Based on the biology of the species and the threats acting on 
it, the foreseeable future used in the determination was 20 to 30 
years. The generation time for the species is 2 years with a life-span 
up to 3.5 years; the period of 20-30 years encompasses 10-15 
generations, which is more than sufficient time to determine the 
species' response to the stressors. Although the future scenarios, 
which were snapshots in time for predicting resiliency, redundancy, and 
representation extended through 2070, the uncertainty as to the 
outcomes with regard to the responses to the stressors became so great 
as to render the scenarios too unreliable beyond 2050 for that time 
period to be considered the foreseeable future.
    Habitat fragmentation and isolation have contributed to the 
partitioning into 13 populations. While the Panama City crayfish faces 
a variety of threats, only one threat, habitat loss and degradation, 
habitat fragmentation, and subpopulation isolation due to urban 
development, was considered an important factor in our assessment of 
the future viability of the Panama City crayfish. Based on our future 
scenarios for urban development, we predict major losses of resiliency, 
representation, and redundancy for Panama City crayfish in the 
foreseeable future. Especially problematic is the predicted complete 
loss of resilience and redundancy from the western populations, which 
reduces half of the representation of Panama City crayfish. These 
combined losses under even the most probable status quo scenario make 
the ability of Panama City crayfish to sustain its populations into the 
foreseeable future questionable assuming current levels of protection 
and management.
    We have carefully assessed the best scientific and commercial 
information available regarding the past, present, and future threats 
to the Panama City crayfish. Habitat loss from development is occurring 
rangewide and has resulted in the fragmentation of the landscape. The 
fragmentation of suitable habitat has caused the isolation of existing 
populations limited to ditches, swales, slash pine plantations, and 
utility rights-of-ways. At the population level, Panama City crayfish 
now exists in 13 populations. Currently, four populations are estimated 
to maintain high resiliency; five are estimated to have moderate 
resiliency; and four are estimated to have low resiliency, including 
the two populations that are in the low condition but were excluded 
from future scenario analysis because of inadequate data.
    At the species level, the 13 Panama City crayfish populations are 
broken down into an eastern group of five populations and a western 
group of eight populations based on the characteristics of Panama City 
crayfish and its geographic distribution. Currently, four populations, 
all in the west, are in low condition, including the two that were 
excluded from future condition analysis because of inadequate data. 
These two populations represent 31 percent of the known populations 
overall and 50 percent of the western group, and, although still in 
existence, they may not contribute to the future redundancy of Panama 
City crayfish, because the populations are already experiencing genetic 
drift and the habitat that supports them is susceptible to future 
development.
    All future scenarios predicted a negative impact on the redundancy 
of Panama City crayfish. Under the ``status quo'' scenario, 62 percent 
of populations are in low condition by 2050; this percentage increases 
to 69 percent under the ``intermediate development'' scenario and to 77 
percent under the ``high development'' scenario. The greatest loss of 
redundancy for Panama City crayfish is

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predicted to occur in the western group. In this group, 100 percent of 
the populations are in low condition by 2050 under the ``high 
development'' scenario and 88 percent under the other two scenarios. In 
the eastern group, three populations are predicted to remain 
strongholds for Panama City crayfish, although they would represent 
only 60 percent of the remaining eastern populations.
    At the species level, we estimate that the Panama City crayfish 
currently has low to moderate adaptive potential across its range, and 
all of the future scenarios are predicted to have an impact on the 
species' representation during the 50-year time horizon. Even though 
Panama City crayfish has low representation in the western group, with 
only two of the eight populations not in low condition, these two 
populations likely will persist because of the protection afforded 
through conservation easements. The eastern group comprises a much 
larger area and contains the three populations currently in high 
condition. However, two of these populations, Highpoint and 231-north, 
are predicted to be in low condition in the future. This is especially 
concerning given that the Highpoint population contains unique genetic 
diversity not found in other populations, although more work is needed 
to confirm this (Duncan et al. 2017, p. 19).
    In short, based on our analysis of the species' current and future 
conditions, as well as the conservation efforts discussed above, we 
conclude that the population and habitat factors used to determine the 
resiliency, representation and redundancy for Panama City crayfish will 
continue to decline so it is likely to become in danger of extinction 
throughout its range within the foreseeable future. Therefore, on the 
basis of the best available scientific and commercial information, we 
propose listing the Panama City crayfish as threatened in accordance 
with sections 3(6) and 4(a)(1) of the Act.
    Under the Act and our implementing regulations, a species may 
warrant listing if it is endangered or threatened throughout all or a 
significant portion of its range. Because we have determined that the 
Panama City crayfish is threatened throughout all of its range, under 
the Final Policy on Interpretation of the Phrase ``Significant Portion 
of Its Range'' in the Endangered Species Act's Definitions of 
``Endangered Species'' and ``Threatened Species'' (79 FR 37577, July 1, 
2014) (SPR Policy), if a species warrants listing throughout all of its 
range, no portion of the species' range can be a ``significant'' 
portion of its range.). While it is the Service's position under the 
SPR Policy that undertaking no further analysis of ``significant 
portion of its range'' in this circumstance is consistent with the 
language of the Act, we recognize that the Policy is currently under 
judicial review, so we also took the additional step of considering 
whether there could be any significant portions of the species' range 
where the species is in danger of extinction. We evaluated whether 
there is substantial information indicating that there are any portions 
of the species' range: (1) That may be ``significant,'' and (2) where 
the species may be in danger of extinction. In practice, a key part of 
identifying portions appropriate for further analysis is whether the 
threats are geographically concentrated. The threats affecting the 
species are throughout its entire range; therefore, there is not a 
meaningful geographical concentration of threats. As a result, even if 
we were to undertake a detailed SPR analysis, there would not be any 
portions of the species' range where the threats are harming the 
species to a greater degree such that it is in danger of extinction in 
that portion.

Critical Habitat

    Section 4(a)(3) of the Act, as amended, and implementing 
regulations in 50 CFR 424.12, require that, to the maximum extent 
prudent and determinable, we designate critical habitat at the time the 
species is determined to be an endangered or threatened species. 
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 in accordance with the Act, upon a 
determination by the Secretary of the Interior that such areas are 
essential for the conservation of the species.
    Our regulations (50 CFR 424.12(a)(1)) state that the designation of 
critical habitat is not prudent when any 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. The regulations also 
provide that, in determining whether a designation of critical habitat 
would not be beneficial to the species, the factors that the Service 
may consider include, but are not limited to, whether the present or 
threatened destruction, modification, or curtailment of a species' 
habitat or range is not a threat to the species, or whether any areas 
meet the definition of ``critical habitat'' (50 CFR 424.12(a)(1)(ii)).
    As discussed above, there is no evidence that collection or 
vandalism are threats to the species, and there is no indication that 
identification and mapping of critical habitat is likely to initiate 
any such threats. Therefore, in the absence of finding that the 
designation of critical habitat would increase threats to the species, 
if there are benefits to the species from a critical habitat 
designation, a finding that designation is prudent is appropriate.
    The potential benefits of designation may 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 unoccupied; (2) focusing conservation 
activities on the most essential features and areas; (3) providing 
educational benefits to State or county governments or to private 
entities; and (4) preventing people from causing inadvertent harm to 
the protected species. Because designation of critical habitat would 
not likely increase the degree of threat to the species and may provide 
some measure of benefit, designation of critical habitat is prudent for 
the Panama City crayfish.
    Our regulations (50 CFR 424.12(a)(2)) further state that critical 
habitat is not determinable when one or both of the following 
situations exists: (1) Information sufficient to perform required 
analysis of the impacts of the designation is lacking; or (2) the 
biological needs of the species are not sufficiently well known to 
permit identification of an area as critical habitat. A careful 
assessment of the economic impacts that may occur due to a critical 
habitat designation is ongoing, and we are in the process of working 
with the States and other partners in acquiring the complex information 
needed to perform that assessment. Until these efforts are complete, 
information sufficient to perform a required analysis of the impacts of 
the designation is lacking, and, therefore, we find designation of 
critical habitat for this species to be not determinable at this time.

Available Conservation Measures

    Conservation measures provided to species listed as endangered or

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threatened species under the Act include recognition, recovery actions, 
requirements for Federal protection, and prohibitions against certain 
practices. Recognition through listing results in public awareness, and 
conservation by Federal, State, Tribal, and local agencies; private 
organizations; and individuals. The Act encourages cooperation with the 
States and other countries and calls for recovery actions to be carried 
out for listed species. The protection required by Federal agencies and 
the prohibitions against certain activities are discussed, in part, 
below.
    The primary purpose of the Act is the conservation of endangered 
and threatened species and the ecosystems upon which they depend. The 
ultimate goal of such conservation efforts is the recovery of these 
listed species, so that they no longer need the protective measures of 
the Act. Subsection 4(f) of the Act calls for the Service to develop 
and implement recovery plans for the conservation of endangered and 
threatened species. The recovery planning process involves the 
identification of actions that are necessary to halt or reverse the 
species' decline by addressing the threats to its survival and 
recovery. The goal of this process is to restore listed species to a 
point where they are secure, self-sustaining, and functioning 
components of their ecosystems.
    Recovery planning includes the development of a recovery outline 
shortly after a species is listed and preparation of a draft and final 
recovery plan. The recovery outline guides the immediate implementation 
of urgent recovery actions and describes the process to be used to 
develop a recovery plan. Revisions of the plan may be done to address 
continuing or new threats to the species, as new substantive 
information becomes available. The recovery plan also identifies 
recovery criteria for review of when a species may be ready for 
downlisting (i.e., reclassification from endangered status to 
threatened status) or delisting (i.e., removal from the List), and 
methods for monitoring recovery progress. Recovery plans also establish 
a framework for agencies to coordinate their recovery efforts and 
provide estimates of the cost of implementing recovery tasks.
    Recovery teams (composed of species experts, Federal and State 
agencies, nongovernmental organizations, and stakeholders) are often 
established to develop recovery plans. When completed, the recovery 
outline, draft recovery plan, and the final recovery plan will be 
available on our website (http://www.fws.gov/endangered), or from our 
Panama City Ecological Services Field Office (see FOR FURTHER 
INFORMATION CONTACT).
    Implementation of recovery actions generally requires the 
participation of a broad range of partners, including other Federal 
agencies, States, Tribes, nongovernmental organizations, businesses, 
and private landowners. Examples of recovery actions include habitat 
restoration (e.g., restoration of native vegetation), research, captive 
propagation and reintroduction, and outreach and education. The 
recovery of many listed species cannot be accomplished solely on 
Federal lands because their ranges may occur primarily or solely on 
non-Federal lands. To achieve recovery of these species requires 
cooperative conservation efforts on private, State, and Tribal lands. 
If this species is listed, funding for recovery actions will be 
available from a variety of sources, including Federal budgets, State 
programs, and cost share grants for non-Federal landowners, the 
academic community, and nongovernmental organizations. In addition, 
pursuant to section 6 of the Act, the State of Florida would be 
eligible for Federal funds to implement management actions that promote 
the protection or recovery of the Panama City crayfish. Information on 
our grant programs that are available to aid species recovery can be 
found at: http://www.fws.gov/grants.
    Although the Panama City crayfish is only proposed for listing 
under the Act at this time, please let us know if you are interested in 
participating in recovery efforts for this species. Additionally, we 
invite you to submit any new information on this species whenever it 
becomes available and any information you may have for recovery 
planning purposes (see FOR FURTHER INFORMATION CONTACT).
    Section 7(a) of the Act requires Federal agencies to evaluate their 
actions with respect to any species that is proposed or listed as an 
endangered or threatened species and with respect to its critical 
habitat, if any is designated. Regulations implementing this 
interagency cooperation provision of the Act are codified at 50 CFR 
part 402. Section 7(a)(4) of the Act requires Federal agencies to 
confer with the Service on any action that is likely to jeopardize the 
continued existence of a species proposed for listing or result in 
destruction or adverse modification of proposed critical habitat. If a 
species is listed subsequently, section 7(a)(2) of the Act requires 
Federal agencies to ensure that activities they authorize, fund, or 
carry out are not likely to jeopardize the continued existence of the 
species or destroy or adversely modify its critical habitat. If a 
Federal action may affect a listed species or its critical habitat, the 
responsible Federal agency must enter into consultation with the 
Service.
    Federal agency actions within the species' habitat that may require 
conference or consultation or both as described in the preceding 
paragraph include management and any other landscape-altering 
activities on Federal lands administered by the issuance of section 404 
Clean Water Act (33 U.S.C. 1251 et seq.) permits by the U.S. Army Corps 
of Engineers, and construction and maintenance of roads or highways by 
the Federal Highway Administration.
    The Act and its implementing regulations set forth a series of 
general prohibitions and exceptions that apply to threatened wildlife. 
The prohibitions of section 9(a)(1) of the Act, as applied to 
threatened wildlife and codified at 50 CFR 17.31, make it illegal for 
any person subject to the jurisdiction of the United States to take 
(which includes harass, harm, pursue, hunt, shoot, wound, kill, trap, 
capture, or collect; or to attempt any of these) threatened wildlife 
within the United States or on the high seas. In addition, it is 
unlawful to import; export; deliver, receive, carry, transport, or ship 
in interstate or foreign commerce in the course of commercial activity; 
or sell or offer for sale in interstate or foreign commerce any listed 
species. It is also illegal to possess, sell, deliver, carry, 
transport, or ship any such wildlife that has been taken illegally. 
Certain exceptions apply to employees of the Service, the National 
Marine Fisheries Service, other Federal land management agencies, and 
State conservation agencies.
    We may issue permits to carry out otherwise prohibited activities 
involving threatened wildlife under certain circumstances. Regulations 
governing permits are codified at 50 CFR 17.32. With regard to 
threatened wildlife, a permit may be issued for the following purposes: 
For scientific purposes, to enhance the propagation or survival of the 
species, for economic hardship, for zoological exhibition, for 
educational purposes, or for other special purposes consistent with the 
purposes of the Act. There are also certain statutory exemptions from 
the prohibitions, which are found in sections 9 and 10 of the Act.
    It is our policy, as published in the Federal Register on July 1, 
1994 (59 FR 34272), to identify to the maximum extent practicable at 
the time a species is listed, those activities that would or would not 
constitute a violation of section 9 of the Act. The intent of this 
policy is to increase public awareness of

[[Page 341]]

the effect of a proposed listing on proposed and ongoing activities 
within the range of the species proposed for listing. Activities that 
the Service believes could potentially harm the Panama City crayfish 
and result in ``take'' include, but are not limited to:
    (1) Unauthorized handling or collecting of the species;
    (2) Destruction or alteration of the species' habitat by 
development;
    (3) Actions that would alter the hydrology within suitable soils 
available for the Panama City crayfish;
    (4) Actions that result in permanent loss of habitat within 
suitable soils once available to the Panama City crayfish;
    (5) Application of chemicals, including insecticides and petroleum 
products in violation of label restrictions, or other actions that 
pollute the soils and waters that are used by the Panama City crayfish; 
and
    (6) Destruction of herbaceous vegetation directly adjacent to 
occupied pools that affects the hydrology and removes cover for the 
crayfish.
    Questions regarding whether specific activities would constitute a 
violation of section 9 of the Act should be directed to the Panama City 
Ecological Services Field Office (see FOR FURTHER INFORMATION CONTACT, 
above).

Required Determinations

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 ADDRESSES. 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.

National Environmental Policy Act (42 U.S.C. 4321 et seq.)

    We have determined that environmental assessments and environmental 
impact statements, as defined under the authority of the National 
Environmental Policy Act, need not be prepared in connection with 
listing a species as an endangered or threatened species 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).

References Cited

    A complete list of references cited in the SSA report is available 
on the internet at http://www.regulations.gov and upon request from the 
Panama City Ecological Services Field Office (see FOR FURTHER 
INFORMATION CONTACT, above).

Authors

    The primary authors of this proposed rule are the staff members of 
the Service's Unified Listing Team and the Panama City 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--ENDANGERED AND THREATENED WILDLIFE AND PLANTS

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. Amend Sec.  17.11(h), the List of Endangered and Threatened 
Wildlife, by adding an entry for ``Crayfish, Panama City'' in 
alphabetical order under CRUSTACEANS to read as set forth below:


Sec.  17.11  Endangered and threatened wildlife.

* * * * *
    (h) * * *

----------------------------------------------------------------------------------------------------------------
                                                                                           Listing citations and
          Common name              Scientific name      Where listed          Status         applicable rules
----------------------------------------------------------------------------------------------------------------
 
                                                  * * * * * * *
----------------------------------------------------------------------------------------------------------------
                                                   CRUSTACEANS
----------------------------------------------------------------------------------------------------------------
 
                                                  * * * * * * *
Crayfish, Panama City..........  Procambarus         Wherever found....  T                [Federal Register
                                  econfinae.                                               citation when
                                                                                           published as a final
                                                                                           rule].
 
                                                  * * * * * * *
----------------------------------------------------------------------------------------------------------------

* * * * *

     Dated: November 21, 2017.
 James W. Kurth,
Deputy Director for U.S. Fish and Wildlife Service Exercising the 
Authority of the Director for U.S. Fish and Wildlife Service.
[FR Doc. 2017-28313 Filed 1-2-18; 8:45 am]
 BILLING CODE 4333-15-P