[Federal Register Volume 80, Number 193 (Tuesday, October 6, 2015)]
[Proposed Rules]
[Pages 60335-60348]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2015-25280]


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DEPARTMENT OF THE INTERIOR

Fish and Wildlife Service

50 CFR Part 17

[Docket No. FWS-R4-ES-2015-0142; 4500030113]
RIN 1018-BB09


Endangered and Threatened Wildlife and Plants; Proposed 
Threatened Species Status for the Suwannee Moccasinshell

AGENCY: Fish and Wildlife Service, Interior.

ACTION: Proposed rule; 12-month finding and status review.

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SUMMARY: We, the U.S. Fish and Wildlife Service (Service), propose to 
list the Suwannee moccasinshell (Medionidus walkeri), a freshwater 
mussel species from the Suwannee River Basin in Florida and Georgia, as 
a threatened species under the Endangered Species Act of 1973, as 
amended (Act). If we finalize this rule as proposed, it would extend 
the Act's protections to this species. The effect of this regulation 
will be to add this species to the List of Endangered and Threatened 
Wildlife.

DATES: We will accept comments received or postmarked on or before 
December 7, 2015. 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 November 20, 2015.

ADDRESSES: 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-2015-0142, 
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-2015-0142; U.S. Fish and Wildlife 
Service Headquarters, 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 T. Phillips, Project Leader, 
U.S. Fish and Wildlife Service, Panama City Ecological Services Field 
Office, 1601 Balboa Avenue, Panama City, FL 32405; by telephone 850-
769-0552; or by facsimile at 850-763-2177. If you use a 
telecommunications device for the deaf (TDD), please call the Federal 
Information Relay Service (FIRS) at 800-877-8339.

SUPPLEMENTARY INFORMATION: 

Executive Summary

    Why we need to publish a rule. Under the Act, 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 of critical 
habitat can only be completed by issuing a rule.
    This rule proposes the listing of the Suwannee moccasinshell 
(Medionidus walkeri) as a threatened species. The Suwannee 
moccasinshell is a candidate species for which we have on file 
sufficient information on biological vulnerability and threats to 
support

[[Page 60336]]

preparation of a listing proposal, but for which development of a 
listing regulation has been precluded by other higher priority listing 
activities. This rule reassesses all available information regarding 
status of and threats to the Suwannee moccasinshell.
    This rule does not propose critical habitat for the Suwannee 
moccasinshell. We have determined that designation of critical habitat 
is prudent, but not determinable at this time because:
     While we have significant information on the habitat of 
the species, we need more information on biological needs of the 
species (i.e., specific habitat features on the landscape) in order to 
identify specific areas appropriate for critical habitat designation.
     In addition, as we have not determined the areas that may 
qualify for designation, the information sufficient to perform a 
required analysis of the impacts of the designation is lacking.
    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 this species is threatened 
by degradation of its habitat due to polluted runoff from agricultural 
lands, discharges from industrial and municipal wastewater sources and 
mining operations, sedimentation, decreased flows due to groundwater 
extraction and drought (Factor A); State and Federal water quality 
standards that are inadequate to protect sensitive aquatic organisms 
like mussels (Factor D); contaminant spills as a result of 
transportation accidents or from industrial, agricultural, and 
municipal facilities (Factor E); increased drought frequency as a 
result of changing climatic conditions (Factor E); greater 
vulnerability to certain threats because of small population size and 
range (Factor E); and competition and disturbance from the introduced 
Asian clam (Factor E).
    We will seek peer review. We will seek comments from independent 
specialists to ensure that our designation is based on scientifically 
sound data, assumptions, and analyses. We will invite these peer 
reviewers to comment on our listing proposal.
    Because we will consider all comments and information received 
during the comment period, our final determinations may differ from 
this proposal.

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 the public, other concerned governmental 
agencies, Native American tribes, the scientific community, industry, 
or any other interested parties concerning this proposed rule. We 
particularly seek comments concerning:
    (1) The Suwannee moccasinshell'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. In particular, we seek 
information concerning the potential threats to the Suwannee 
moccasinshell, including:
    (a) The effects of pesticides and their ingredients and metabolites 
on the species;
    (b) The impact of diseases on the species;
    (c) The impact of flood scour on the species and its habitat; and
    (d) The impact of introduced flathead catfish on fishes needed by 
the species to reproduce.
    (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.
    Please include sufficient information with your submission (such as 
scientific journal articles or other publications) to allow us to 
verify any scientific or commercial information you include.
    Please note that submissions merely stating support for or 
opposition to the action under consideration without providing 
supporting information, although noted, will not be considered in 
making a determination, as section 4(b)(1)(A) of the Act directs that 
determinations as to whether any species is a threatened or endangered 
species must be made ``solely on the basis of the best scientific and 
commercial data available.''
    You may submit your comments and materials concerning this proposed 
rule by one of the methods listed in 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 Web site. If your submission is made via a hardcopy 
that includes personal identifying information, you may request at the 
top of your document that we withhold this information from public 
review. However, we cannot guarantee that we will be able to do so. We 
will post all hardcopy submissions on 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 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 within 45 
days after the date of publication of this proposed rule in the Federal 
Register. Such requests must be sent to the address shown in 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), we are seeking the 
expert opinions of three appropriate and independent specialists 
regarding this proposed rule.

[[Page 60337]]

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 Suwannee moccasinshell biology, 
habitat, physical or biological factors, etc., and are currently 
reviewing the species status report, which will inform our 
determination. We invite comment from the peer reviewers during this 
public comment period.

Previous Federal Actions

    We identified the Suwannee moccasinshell (Medionidus walkeri) as a 
Category 2 species in the Candidate Notice of Review (CNOR) published 
in the Federal Register of November 15, 1994 (59 FR 58982). Category 2 
candidates were defined as species for which we had information that 
proposed listing was possibly appropriate, but for which conclusive 
data on biological vulnerability and threats were not available to 
support a proposed rule at the time. In the February 28, 1996, CNOR (61 
FR 7596), we discontinued the designation of Category 2 species as 
candidates; therefore, the Suwannee moccasinshell was no longer a 
candidate species.
    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. On September 27, 2011, the 
Service published a substantial 90-day finding for 374 of the 404 
species, including the Suwannee moccasinshell, soliciting information 
about, and initiating status reviews for, those species (76 FR 59836). 
In 2013, CBD filed a complaint against the Service for failure to 
complete a 12-month finding for the Suwannee moccasinshell within the 
statutory timeframe. In 2014, 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 Suwannee 
moccasinshell would be delivered to the Federal Register by September 
30, 2015.

Background

Taxonomy and Species Description

    The Suwannee moccasinshell (Medionidus walkeri) is a freshwater 
mussel of the family Unionidae. The species was originally described by 
B.H. Wright in 1897; it was briefly considered a synonym of Medionidus 
penicillatus (Clench and Turner 1956), but subsequently was recognized 
as a valid species by Johnson (1977, p. 176). Its distinctiveness as a 
separate species is recognized by recent authors (Williams and Butler 
1994, p. 85; Williams et al. 2014, p. 278). Its sharp posterior ridge 
and generally dark, rayless shell distinguishes it from other species 
of Medionidus in Gulf drainages (Johnson 1977, p. 177; Williams and 
Butler 1994, p. 86).
    The Suwannee moccasinshell is a small mussel that rarely exceeds 50 
millimeters (2.0 inches) in length. Its shell is oval in shape and 
sculptured with corrugations extending along the posterior ridge, 
although the corrugations are sometimes faint. The shell exterior 
(periostracum) is greenish yellow to brown with green rays of varying 
width and intensity in young individuals, and olive brown to brownish 
black with rays often obscured in mature individuals (Williams et al. 
2014, p. 278). The sexes can be distinguished, with female shells being 
smaller and longer than the males (Johnson 1977, p. 177). The Suwannee 
moccasinshell is easily distinguished from all other mussels in the 
Suwannee River Basin by having an oval outline and sculpture on the 
posterior slope (Williams et al. 2014, p. 279).

Evaluation of Listable Entity

    Under the Act, the term ``species'' includes any subspecies of fish 
or wildlife or plants, and any distinct population segment of any 
species of vertebrate fish or wildlife which interbreeds when mature 
(16 U.S.C. 1532(16)). Based on our review of the best available 
scientific and commercial information (see Taxonomy and Species 
Description above) the taxonomic entity that is known as Suwannee 
moccasinshell (Medionidus walkeri) is a distinct species. Therefore, we 
conclude that the Suwannee moccasinshell does meet the definition of a 
species under section 3(16) of the Act, and that the petitioned entity 
does constitute a listable entity and can be listed under the Act.

Habitat and Biology

    Unionid mussels live in the bottom substrates of streams and lakes 
where they generally burrow completely into the substrate and orient 
themselves near the substrate surface to take in food and oxygen. The 
Suwannee moccasinshell typically inhabits larger streams where it is 
found in substrates of muddy sand or sand with some gravel, and in 
areas with slow to moderate current (Williams and Butler 1994, p. 86; 
Williams 2015, p. 2). Recent surveys by the Florida Fish and Wildlife 
Conservation Commission (FFWCC) for the species in the Suwannee River 
main channel found individuals at depths ranging from around 0.5 to 2.5 
meters (1.6 to 8.2 ft) (FFWCC 2014 unpub. data). Based on stream 
conditions in areas that still support the species, suitable Suwannee 
moccasinshell habitat appears to be clear stream reaches along bank 
margins with a moderate slope and stable sand substrates, where flow is 
moderate and slightly depositional conditions exist. These are ideal 
habitat conditions for most mussels in the main channel, and several 
species occur in areas where the Suwannee moccasinshell is found. In 
addition, the Suwannee moccasinshell is associated with large woody 
material, and individuals are often found near embedded logs. These 
attributes also likely indicate the habitat preferences of its host 
fishes.
    Adult mussels obtain food items both from the water column and from 
the sediments. They filter feed by taking water in through the 
incurrent siphon and across four gills that are specialized for 
respiration and food collection. They can also move sediment material 
into the shell by using cilia (hair-like structures) on the foot or 
through currents created by cilia. Juvenile mussels typically burrow 
completely beneath the substrate surface for the first several months 
of their life. During this time, they feed primarily with their 
ciliated foot, which they sweep through the sediment to extract 
material, until the structures for filter feeding are more fully 
developed. Mussels feed on a variety of microscopic food particles that 
include algae, diatoms, bacteria, and fine detritus (disintegrated 
organic debris) (McMahon and Bogan 2001, p. 331; Strayer et al. 2004, 
pp. 430-431, Vaughn et al. 2008, p. 410).
    Spawning in freshwater mussels general occurs from spring to late 
summer (Haag 2012, p. 38). Water temperature appears to be the primary 
cue for spawning (McMahon and Bogan 2001, p. 343; Galbraith and Vaughn 
2009, p. 42). During spawning, males release sperm into the water 
column, which females take in through their inhalant aperture during 
feeding. Fertilization takes place inside the gills, and females brood 
the fertilized eggs in modified portions of one or both pairs of gills 
until they develop into mature larvae called glochidia. The timing and 
duration of the brooding period varies by species, but can be 
classified as either short term or long term. In short-term brooders, 
glochidia are released as soon as they are mature, generally 2-6 weeks 
after fertilization. In long-term brooders, the mature glochidia are 
brooded over the winter and released the following spring or summer.
    Reproduction in unionid mussels is remarkable in that the glochidia 
of most

[[Page 60338]]

species must attach to a fish host in order to transform into a 
juvenile mussel. Many mussel species use only one or a few specific 
fish species as hosts, and have evolved lures to attract a particular 
fish species or group of related fish species (Haag 2012, p. 42). 
Females of some mussel species release their glochidia, either 
individually (sometimes in mucus strands for suspension), in packets 
termed conglutinates, which resemble fish food items, or in one large 
mass known as a superconglutinate, which resembles a small fish 
(Barnhart et al. 2008, pp. 374-379). In other species, female mussels 
transmit glochidia directly to the host fish by using mantel flap lures 
to entice an attack (Barnhart et al. 2008, p. 380) and expel glochidia 
into the host's mouth.
    The number of glochidia released by a female in one reproductive 
cycle can range from several thousand to several million and is 
extremely variable among species (Haag 2012, p. 196). The variation is 
related to body size with larger females producing more eggs than 
smaller individuals (Haag 2012, pp. 200-206). If the glochidia 
encounter a fish, they attempt to clamp onto the gills, fins, or skin. 
Glochidia that attach to a suitable host encyst in the tissues and 
undergo a metamorphosis. The duration of the encystment varies by 
mussel species, usually lasting from 2-4 weeks, but can last for 
several months (Haag 2012, p. 42). When the metamorphosis is complete, 
the juveniles drop from the host and sink to the bottom to begin life 
as a free-living mussel.
    Parasitism primarily serves as a means of upstream dispersal for 
this relatively sedentary group of organisms (Haag 2012, p. 145). The 
intimate relationship between freshwater mussels and their host fish 
plays a major role in mussel distributions on both a landscape and 
community scale. Haag and Warren (1998, p. 304) determined that mussel 
community composition was more a function of fish community pattern 
variability than of microhabitat variability, and that the type of 
strategy used by mussels for infecting host fishes was the determining 
factor.
    An ongoing study has provided preliminary information about the 
reproductive biology of the Suwannee moccasinshell. Females were found 
gravid with mature glochidia from December to February, and also in 
late May/early June (Johnson 2015 unpub. data). In laboratory trials, 
Suwannee moccasinshell glochidia transformed primarily on the 
blackbanded darter (Percina nigrofasciata) and to a lesser extent on 
the brown darter (Etheostoma edwini) (Johnson 2015 unpub. data). Six 
other fish species from 5 families were also tested but none 
transformed moccasinshell larvae. This indicates that the Suwannee 
moccasinshell is a host specialist and dependent on darters for 
reproduction, and is consistent with other members of the genus 
Medionidus, which also use only darters (Percidae) as hosts (Haag and 
Warren 2003, p. 82; Fritts and Bringolf 2014, p. 54). To attract its 
darter host, the moccasinshell uses a small mantel lure consisting of a 
vibrant blue patch on the mantel interior that it flashes while 
wiggling papillae on the mantel margin (Johnson 2015 unpub. data). 
Darters are small, bottom-dwelling fish that generally do not move 
considerable distances (Freeman 1995, pp. 363-365; Holt 2013, p. 657). 
Thus, the exclusive use of darters as a host may limit the Suwannee 
moccasinshell's ability to disperse, and to recolonize some areas from 
which it has become extirpated.

Distribution and Abundance

    The Suwannee moccasinshell is endemic to the Suwannee River Basin 
in Florida and Georgia. The Suwannee River Basin is a unique river 
system, characterized by blackwater streams in its headwaters and 
numerous springs (over 300) in its middle and lower reaches. The river 
originates in the Okefenokee Swamp and meanders more than 400 
kilometers through south-central Georgia and north-central Florida 
before emptying into the Gulf of Mexico. There are three large 
tributaries to the Suwannee River--the Alapaha, Withlacoochee, and 
Santa Fe Rivers. The Suwannee moccasinshell's historical range includes 
the lower and middle Suwannee River proper, the Santa Fe River sub-
basin, and the lower reach of the Withlacoochee River (Williams 2015, 
p. 7). There are no freshwater mussels in the upper Suwannee River 
Basin (upstream of the mouth of Swift Creek) due to naturally low pH 
and nutrient levels (Williams et al. 2014, p. 62). Within the Suwannee 
River mainstem, the species is historically known from the mouth of 
Manatee Springs run, upstream to the vicinity of the junction of the 
Withlacoochee River. Within the Santa Fe sub-basin, the species is 
known from several locations in the Santa Fe River, one location in the 
New River (a headwater tributary), and one location in a small unnamed 
tributary to the New River. In the Withlacoochee River, it is known 
from three historical locations in the lower reach of the river.
    There is a single record of the species from the Hillsborough River 
Basin, a small river basin in Florida that empties into Tampa Bay, 
collected by van Hyning in 1932 (Williams et al. 2014, p. 280). 
However, recent information obtained while examining specimens in the 
collection of the University of Michigan's Museum of Zoology calls the 
record into question. There is a possibility that the specimen, along 
with at least two other species, were actually collected from the 
Suwannee River and mislabeled (Williams 2015a in litt.). Incorrect 
locality data seems plausible considering that none of the three 
species have been found in the basin before or since the van Hyning 
collection (Williams 2015, p. 3; Williams 2015a in litt.). Therefore, 
the Hillsborough River is not considered part of the Suwannee 
moccasinshell's range at this time, and further research is under way 
that may clarify this situation.
    The Suwannee moccasinshell's range has declined in recent decades, 
and it is presently known only from the Suwannee River main channel and 
the lower Santa Fe River in Florida. Recent occurrence is based on 
collections made from 2000 to 2015. Within the Suwannee mainstem, the 
moccasinshell occurs intermittently throughout a 75-mile (121-
kilometer) reach of the lower and middle river from river mile (RM) 50 
in Dixie/Gilchrist Counties, upstream to RM 125, near the Withlacoochee 
River mouth. A shell fragment was collected in 2015 approximately 7 
miles downstream of the mouth of Manatee Springs run (Williams 2015b in 
litt.). The fragment was estimated to be several years old, and 
additional survey work is needed; however, if the species is found to 
occur in this area, its distribution would be extended downstream by 
several miles. Within the Santa Fe sub-basin, the species is currently 
known from four localities (two are shell material only) in a 28-mile 
segment of the lower Santa Fe River downstream of the rise. The Santa 
Fe River runs underground for about 5 miles and ``rises'' back to the 
surface in Alachua County. The species was not detected in recent 
surveys in the Withlacoochee River or in the upper Santa Fe sub-basin 
(upstream of the rise), which includes its tributary, the New River. 
The species has not been collected in the past 50 years in the 
Withlacoochee River; however, the lower reach of the river continues to 
support good mussel diversity (Williams 2015, p. 3), and additional 
survey work is needed to verify if it is extirpated in this sub-basin.
    Targeted surveys by FFWCC biologists in 2013 and 2014 show that 
Suwannee moccasinshell numbers are low.

[[Page 60339]]

Experienced mussel biologists surveyed 96 sites, covering most of its 
historical range, and collected a total of 67 live individuals at 21 
sites, all from the Suwannee River main channel. Fourteen individuals 
were collected at one location, but at most sites 3 or fewer 
individuals were found (FFWCC 2014 unpub. data). At locations where the 
species was detected, it comprised only 1 percent of the mussel sample. 
In April of 2015, FFWCC biologists surveyed 14 sites in the lower Santa 
Fe River, and encountered only 1 Suwannee moccasinshell out of 1,880 
mussels collected during the survey (Holcomb 2015 in litt.). A summary 
of occurrence, distribution, and abundance of Suwannee moccasinshell 
populations by waterbody are shown in Table 1 below.

                       Table 1--Summary of Suwannee Moccasinshell Populations by Waterbody
----------------------------------------------------------------------------------------------------------------
                                                                                            Distribution and
             Water body                   State and county           Occurrence *               abundance
----------------------------------------------------------------------------------------------------------------
Suwannee River mainstem.............  FL: Madison Suwannee,    Recent.................  Occurs in a 75-mile
                                       Lafayette, Gilchrist,                             reach; 67 individuals
                                       Dixie, Levy,.                                     at 21 sites; abundance
                                                                                         low but population is
                                                                                         stable.
Santa Fe River......................  FL: Suwannee,            Recent.................  Occurs in 28-mile reach
                                       Gilchrist, Columbia,                              in lower river; 2
                                       Alachua, Union,                                   individuals at 2 sites;
                                       Bradford.                                         drastic decline and
                                                                                         abundance very low.
New River, and unnamed trib. to New   FL: Union, Alachua,      Historical.............  May be extirpated; last
 River.                                Bradford.                                         collected in system in
                                                                                         1996.
Withlacoochee River.................  GA: Brooks, Lowndes;     Historical.............  May be extirpated; last
                                       FL: Madison, Hamilton.                            collected in system in
                                                                                         1969.
----------------------------------------------------------------------------------------------------------------
* Recent occurrence is based on collections made from 2000 to 2015; historical occurrence is based on
  collections made prior to 2000.

    Historical mussel collection data are often limited, making it 
difficult to compare trends in abundance over time. Available 
historical collection data seem to indicate that the species was more 
abundant at one time as several museum lots contain 20 or more 
individuals. However, it is difficult to compare historical collections 
to recent collections, as survey efforts for these collections (and for 
most early mussel collections) are unknown, and sometimes museum lots 
are split or combined. It does seem clear from museum collections that 
Suwannee moccasinshell numbers in the Santa Fe River sub-basin have 
declined dramatically in recent decades. Three lots in the Florida 
Museum of Natural History (4,133; 4,159; 4,160) collected from the 
Santa Fe River in 1934 contain a total of 70 individuals. In 
comparison, only two live moccasinshells have been collected in the 
entire Santa Fe River sub-basin since 2000 (one in 2012 and another in 
2015) despite considerable survey effort in areas where the species 
historically occurred.
    In summary, an evaluation of historical and recent collection data 
show the Suwannee moccasinshell has undergone a reduction in range, and 
may no longer persist at several locations where it historically 
occurred. The species may be extirpated from the Withlacoochee River, 
and its range and abundance have clearly declined in the Santa Fe River 
system, where it is now found only in the lower portion of the Santa Fe 
River mainstem in exceedingly low abundance. In addition, the species 
may not be able to reestablish populations in some areas due to its 
limited ability to disperse. The Suwannee moccasinshell continues to 
occur throughout most of its known range in the Suwannee River 
mainstem; however, its numbers are likely lower now than a few decades 
ago. Despite its low abundance, populations in the Suwannee River 
mainstem presently appear to be stable. We attribute its persistence in 
this reach to the stability of the streambed and habitat due to the 
prevalence of geomorphically stable limestone in the channel, and to 
the absence of excessive sedimentation. Also, certain threats such as 
contaminants and reduced flows are likely attenuated in the mainstem 
due to the larger volume of water (threats are discussed in detail in 
the following section).

Summary of Information Pertaining to the Five Factors

    Section 4 of the Endangered Species Act (16 U.S.C. 1533) (ESA, Act) 
and its implementing regulations (50 CFR 424) set forth procedures for 
adding species to the Federal List of Endangered and Threatened 
Wildlife. Under section 4(a)(1) of the Act, we may determine that a 
species is endangered or threatened based on any of the following 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.
    In making this finding, information pertaining to the Suwannee 
moccasinshell in relation to the five factors provided in section 
4(a)(1) of the Act is discussed below. In considering what factors 
might constitute threats to this species, we must look beyond the 
exposure of the species to a particular factor to evaluate whether the 
species may respond to that factor in a way that causes actual impacts 
to the species. If there is exposure to a factor and the species 
responds negatively, the factor may be a threat and, during the status 
review, we attempt to determine how significant a threat it is. The 
threat is significant if it drives, or contributes to, the risk of 
extinction of the species so that the species warrants listing as an 
endangered or threatened species as those terms are defined in the Act. 
However, the identification of factors that could impact a species 
negatively may not be sufficient to compel a finding that the species 
warrants listing. The information must include evidence sufficient to 
suggest that these factors are threats that operate on the species to 
the point that the species may meet the definition of an endangered or 
threatened species under the Act.

Factor A. The Present or Threatened Destruction, Modification, or 
Curtailment of Its Habitat or Range

    The stream habitats of freshwater mussels are vulnerable to 
degradation and modification from a number of threats associated with 
modern civilization. Within the Suwannee River Basin, a rapidly growing 
human population and changing land use represent significant threats to 
the aquatic ecosystem, primarily through pollution and water withdrawal 
(Katz and Raabe 2005, p. 14). The Suwannee moccasinshell's habitat is 
subject to degradation as a result of polluted runoff from croplands 
and poultry and dairy operations, discharges from industries, mines, 
and sewage treatment facilities, and from decreased flows due

[[Page 60340]]

to groundwater extraction (pumping) (Williams 2015, pp. 7-10). Based on 
our current knowledge of the Suwannee moccasinshell and related mussel 
species, the habitat characteristics needed to sustain healthy 
populations generally include (1) stable stream channels and banks; (2) 
stable bottom substrates that are free of excessive algae growth; (3) 
flows that are adequate to maintain benthic habitats, provide food and 
oxygen, transport sperm, and remove wastes; (4) good water quality 
including normal temperature, conductivity, and pH ranges, and adequate 
oxygen content; and (5) an environment free of toxic levels of 
pollutants.

Pollution

    Water quality in the basin has been impaired due to a number of 
point and nonpoint sources of pollutants. As a group, mussels are more 
sensitive to pollution than many other aquatic organisms, and are one 
of the first species to respond to water quality impacts (Haag 2012, p. 
355). Descriptions of localized mortality resulting from chemical 
spills and other discrete point source discharges have been reported. 
However, rangewide decreases in mussel density and diversity may result 
from the more damaging effects of chronic, low-level contamination 
(Newton 2003, p. 2,543; Newton et al. 2003, p. 2,554). There is no 
specific information on the sensitivity of the Suwannee moccasinshell 
to common agricultural, municipal, and industrial pollutants. A 
multitude of bioassays conducted on other mussels show that freshwater 
mussels, especially in early life stages, are more sensitive than 
previously known to some pollutants including chlorine, ammonia, 
copper, nickel, fungicides, and surfactants used in pesticides and 
household products (Keller and Zam 1991, p. 542; Jacobson et al. 1993, 
pp. 879-883; Jacobson et al. 1997, pp. 2,387-2,389; Augspurger et al. 
2003, pp. 2,571-2,574; Wang et al. 2007, pp. 2,039-2,046; Gibson 2015, 
pp. 90-91).
    Ammonia poses a serious threat to mussels due to its ubiquity in 
aquatic systems and its high toxicity to aquatic organisms. It 
originates primarily from agricultural sources (from fertilizers, which 
are often applied as ammonia and animal wastes), but also from 
municipal and industrial wastewater, and atmospheric deposition. 
Although ammonia may be taken up by plants or converted to less toxic 
nitrates by naturally occurring nitrifying bacteria, nitrates also have 
harmful effects on juvenile and adult mussels and may act as endocrine 
disrupters (Bauer 1988, p. 244; Patzner and Muller 2001, pp. 330-333; 
Pelley 2003, p. 162; Camargo and Alonso 2006, pp. 831-849). Moreover, 
ammonia may occur in sediments at greater concentrations than the water 
column (Frazier et al. 1996, pp. 92-99); such occurrences may go 
undetected by common water quality monitoring methods, but may have 
lethal or sublethal effects on mussels (Augspurger et al. 2003, pp. 
2,571-2,574; Wang et al. 2007, pp. 2,039-2046), which burrow and feed 
(with their foot) in sediments. The Environmental Protection Agency 
(EPA) recently revised its water quality standards to levels considered 
protective of freshwater mollusks, but it will be several years before 
facilities must comply with the new limits (see discussion under Factor 
D).
    Pesticides are other widespread contaminants that have long been 
implicated in mussel declines. Pesticides have been linked to 
freshwater mussel die-offs (Fleming et al. 1995, pp. 877-879), and lab 
studies show that mussel glochidia and juveniles are particularly 
sensitive to common pesticides (Conners and Black 2004, pp. 362-371; 
Bringolf et al. 2007a, pp. 2,089-2,093). A surfactant (MON 0818) used 
in the common herbicide Roundup[supreg] was found to be severely toxic 
to juvenile mussels and glochidia (Bringolf et al. 2007b, pp. 2,096-
2,097). The potential role of pesticides in mussel declines has 
received more attention in recent years, but the full range of long-
term effects of pesticides, and their ingredients and metabolites, 
remain unknown (Haag 2012, pp. 374-379).
    An emerging category of contaminant threats to aquatic species is 
pharmaceuticals, including birth control drugs, antidepressants, and 
livestock growth hormones originating from municipal, agricultural, and 
industrial wastewater sources. These chemicals may act as endocrine 
disrupters and can affect mussel reproduction in a number of ways, 
including causing feminization of male mussels (Gagne et al. 2001, pp. 
260-268; Gagne et al. 2011, pp. 99-106).
    High levels of nutrients such as nitrogen and phosphorus may 
indirectly impact mussels by stimulating algae growth. In excess, these 
nutrients lead to algal blooms, which deplete oxygen and can also cause 
dense mats of filamentous algae to form that can entrain juvenile 
mussels (Hartfield and Hartfield 1996, p. 373). Juveniles may be 
particularly sensitive to hypoxic (oxygen-deprived) and eutrophic 
(nutrient-rich) conditions since they inhabit interstitial spaces in 
stream substrates rather than the sediment surfaces occupied by adults 
(Sparks and Strayer 1998, pp. 132-133).
    As discussed under Factor D below, State and Federal regulatory 
mechanisms have helped to reduce the negative effects of point source 
discharges since the 1970s, yet discharges continue to impact water 
quality in the Suwannee River Basin. There are 246 National Pollutant 
Discharge Elimination System (NPDES) permitted facilities within the 
basin; most of them discharge into streams that ultimately flow into 
the middle and lower Suwannee River main channel where the majority of 
the moccasinshell population occurs. According to 2014 monitoring data, 
the top pollutants discharged into the Suwannee River Basin by weight 
were (in decreasing order of value) total suspended solids, nitrogen, 
phosphorus, fluoride, and ammonia (EPA 2014). Additionally, the toxic-
weighted pound equivalent (TWPE), used to compare the potential toxic 
nature of one pollutant to another, indicates that the most hazardous 
pollutants discharged into the Suwannee River Basin are (in decreasing 
order of toxicity) toxaphene (a pesticide), fluoride, chlorine, iron, 
and ammonia (EPA 2014). In previous years, top toxicants discharged 
into the basin also included copper and cyanide.
    Facilities permitted to discharge substantial amounts of wastewater 
into areas that may affect Suwannee moccasinshell populations include 
the Valdosta wastewater treatment plant (WWTP), which is permitted to 
discharge 12 million gallons per day (mgd) to the Withlacoochee River 
in Lowndes County, GA; Packaging Corp. of America, which is permitted 
to discharge 55 mgd to the Withlacoochee River in Lowndes County, GA; 
PCS Phosphate Company, Inc., which is permitted to discharge 200 mgd to 
creeks that flow to the Suwannee River in Hamilton County, FL; Florida 
Power Corp., which is permitted to discharge 342 mgd to the Suwannee 
River in Suwannee County, FL; and Pilgrim's Pride Poultry Processing 
Facility, which is permitted to discharge 1.5 mgd to the Suwannee River 
in Suwannee County, FL (EPA 2014).
    Pollutants released by these facilities in 2014, and considered 
significant (either because of the amount or potential to affect 
mussels) include total suspended solids, nitrogen, phosphorus, ammonia, 
fluoride, iron, and copper (EPA 2014). In addition, spills of municipal 
wastewater at the treatment plant in Valdosta, GA, have leaked 
untreated sewage into the Withlacoochee River on multiple

[[Page 60341]]

occasions. This facility has been a source of periodic releases of 
millions of gallons of untreated sewage, the most recent occurring in 
the summer of 2013 (Williams 2015, p. 8). This issue is currently being 
addressed by the City of Valdosta, which is making numerous 
improvements, including a new WWTP, which is scheduled for completion 
in 2016. PCS Phosphate Company, Inc., is a large phosphate strip mining 
and fertilizer manufacturing operation near White Springs, FL. The 
facility is currently permitted to discharge effluent into creeks that 
flow to the Suwannee River, but surface runoff and periodic overflow of 
settling ponds as a result of heavy rain events may have resulted in 
inputs of total suspended solids, phosphorus, and ammonia into the 
river (Williams 2015, p. 8).
    Nonpoint source pollution is another significant threat throughout 
the Suwannee Basin, entering the system by surface runoff or through 
groundwater. Nonpoint source impacts are attributable primarily to the 
conversion of forests and wetlands to agricultural lands; agriculture 
accounts for most of the developed land uses within the basin, and 
includes silviculture, row crops, and pasture (Katz and Raabe 2005, p. 
9). Surface runoff from these lands may transport numerous pollutants 
including pesticides, fertilizers, metals, sediments, and pathogens 
into stream channels. Surface drainage is more prevalent in the upper 
two-thirds of the basin and the upper Santa Fe River sub-basin where 
the soils are resistant to infiltration (Katz and Raabe 2005, p. 5).
    Pollutants can also enter stream channels via groundwater inflow. 
The Suwannee River Basin has the highest density of springs globally 
(FDEP 2003, p. 29). The majority of flow in the middle Suwannee River 
Basin originates from groundwater sources, as the region is highly 
connected to the underlying Floridan aquifer (FDEP 1985, p. iv). This 
is evidenced by the relative lack of surface water bodies in the middle 
Suwannee River Basin since most water flows through the overlying karst 
features and directly into the aquifer (FDEP 2003, p. 27). For these 
reasons, the middle and lower portions of the Basin are particularly 
vulnerable to groundwater contamination. Katz et al. (1999, pp. 49-50) 
observed groundwater nitrate levels that were seven times greater than 
background levels in areas dominated by cropland, and estimate that it 
may take several decades for nitrogen concentrations to return to their 
original state. Additionally, all nine springs in the basin monitored 
by the Florida Department of Environmental Protection (FDEP) from 2012-
2013 exceeded the nitrate criterion for spring vents (FDEP 2014a, p. 
228), suggesting that contamination is persistent and widespread in the 
central and lower Suwannee River Basin.
    Trends suggest that certain nonpoint source pollutants are becoming 
more abundant in the Suwannee River Basin. According to FDEP (2003, pp. 
76, 83) nitrates are by far the biggest water quality concern in the 
middle and lower portions of the Suwannee Basin. Total estimated 
nitrogen increased continuously from 1955 to 1997 in Gilchrist and 
Lafayette counties (Katz et al. 1999, pp. 45-48). Nitrates have been 
monitored at the U.S. Geological Survey (USGS) monitoring site at 
Branford, FL, since 1954 and the overall trend is increasing (Thom et 
al. 2015, p. 100). Of seven Florida surface water quality stations 
monitored by FDEP in the basin during 1999-2012, increases in total 
nitrogen were observed at four sites, levels of algae and nitrates 
increased at three sites, and phosphorus and fecal coliform increased 
at two sites (FDEP 2014a, pp. 106-123). Nitrogen levels in the Suwannee 
River Basin have likely increased due to nonpoint sources such as 
runoff from croplands, dairy farms, and poultry facilities (Katz et al. 
1999, p. 49). Fertilizer use in the area probably peaked in the late 
1970s (FDEP 2008, pp. 95-100), yet fertilizer-based nitrogen inputs 
remain high and have increased in parts of the Suwannee River Basin 
(Katz et al. 1999, pp. 49-50; FDEP 2014a, pp. 106-123).
    For the 2000 water year, the FDEP determined that the middle 
Suwannee and lower Santa Fe watersheds contributed more than three-
quarters of the basin-wide nitrate-nitrogen load, although these 
watersheds comprise less than 20 percent of the drainage area (FDEP 
2003, p. 35). In 2007, the FDEP (2008, pp. 40-41) found that more than 
40 percent of total nitrogen in the middle and lower Suwannee River 
Basin originates from fertilizer inputs, but also that dairy, poultry, 
and beef production are prominent nitrogen contributors in the area. 
The same report showed that atmospheric deposition contributed less 
than 20 percent of total nitrogen in the area (FDEP 2008, pp. 40-41), 
suggesting that modern nitrogen concentrations in the basin greatly 
surpass historical background levels. In addition, the area is also 
naturally rich in phosphorus, and active and inactive phosphate mining 
operations exist in the central part of the basin. Historically, 
discharges from phosphate-fertilizer production have been correlated 
with major changes in physiochemical properties of basin waters. Spikes 
in total phosphorus, fluoride, and soluble inorganic nitrogen, as well 
as depressed dissolved oxygen (DO) levels, were observed immediately 
downstream of the mouth of Swift Creek, a tributary accepting phosphate 
mine effluent (FDEP 1985, pp. iv-19).
    Section 303(d) of the Clean Water Act (33 U.S.C. 1251 et seq.) 
requires States to identify waters that do not fully support their 
designated use classification. These impaired waters are placed on the 
State's 303(d) list, and a total maximum daily load (TMDL) must be 
developed for the pollutant of concern. A TMDL is an estimate of the 
total load of pollutants that a segment of water can receive without 
exceeding applicable water quality criteria. The Georgia Environmental 
Protection Division's (GEPD) draft 303(d) list for 2014 identifies a 
total of 64 impaired stream segments (a total of 695 stream miles) 
within the Suwannee River Basin (GEPD 2014, pp. 263-273). The list of 
causes of impairment with established TMDLs in Georgia include mercury, 
lead, low dissolved oxygen (DO), fecal coliform, pH, algae, and 
condition of the macroinvertebrate community (GEPD 2014, pp. 263-273). 
The potential sources of these violations are primarily attributed to 
nonpoint or unknown sources but also to municipal facilities and urban 
runoff. FDEP's 303(d) list identifies 52 impaired stream segments or 
water bodies in the Suwannee River Basin. Florida's list identifies 
coliform bacteria, specific conductance, dissolved oxygen, nutrients, 
and unionized ammonia as impaired parameters (FDEP 2014b). Impairments 
within the range of the Suwannee moccasinshell include mercury in the 
lower Suwannee River, and DO and nutrients (algal mats) in the lower 
Santa Fe River (FDEP 2003 pp. 138-139).

Water Withdrawals

    Perhaps the most significant threat to the Suwannee moccasinshell 
is flow reduction due to the withdrawal of groundwater for agricultural 
purposes. Stream flows in the Suwannee River Basin are heavily 
dependent on groundwater contributions. Sufficient groundwater flows 
are essential for maintaining good mussel habitat in the Basin 
(Williams et al. 2014, p. 46). In the past 25 years, center pivot 
irrigation has increased in the Apalachicola-Chattahoochee-Flint (ACF) 
River Basin which borders the Suwannee River Basin to the northwest 
(Torak et al. 2010, p. 2). Most of the groundwater used for irrigation 
in the ACF Basin is withdrawn from the Upper Floridan aquifer. 
Increased pumping in the ACF Basin has lowered groundwater levels

[[Page 60342]]

along the boundary with neighboring Ochlockonee and Suwannee River 
Basins by more than 24 feet. In southeastern Colquitt County, GA, the 
aquifer has experienced unprecedented 40- to 50-foot declines since 
1969 (Torak et al. 2010, p. 44). Periods of extreme dry conditions 
causing insufficient recharging flows into the Upper Floridan aquifer 
occurred in the 1980s-2000s (Torak et al. 2010, p. 47). The lower 
aquifer levels reduced the hydraulic gradient, thus the amount of 
groundwater flowing south and east into the Suwannee Basin (Torak et 
al. 2010, pp. 2, 40).
    Declines in groundwater levels have the potential to lower stream 
base flows by decreasing the amount groundwater discharged to streams. 
This may also reduce high-magnitude flows (10,000-15,000-cubic feet per 
second), which could decrease floodplain connectivity and the transfer 
of matter and energy from overbank to riverine systems (Light et al. 
2002, p. 85; Pringle 2003, entire). Mean annual flow discharge in the 
lower Suwannee River near Wilcox, FL, has declined more than 30 percent 
between 1942 and 2012 (USGS 2014). Similar discharge declines of 
approximately 30 percent have been observed in the Santa Fe River near 
Fort White between 1928 and 2013 (USGS 2014). Reductions in flow can 
alter hydraulically mediated sediment sorting throughout the river, 
which may displace or otherwise alter habitat for Suwannee 
moccasinshell and its host fishes. Groundwater pumping during long 
periods of drought can result in extremely reduced flow rates. The 
upper reaches of the Santa Fe River mainstem and the New River, a major 
tributary, have ceased to flow due to groundwater pumping during 
drought (Williams 2015, p. 9). Biologists conducting mussel surveys on 
the Santa Fe River near Worthington Springs during a dry period in June 
2011 observed that a section of the channel was completely dewatered 
(FFWCC 2011a, p. 2). While pumping does not completely dewater the 
Withlacoochee River, flow rates are greatly reduced (Williams 2015 p. 
9). Reduced flows may exacerbate drought conditions (elevating 
temperature, pH, and pollutant concentrations (causing biotic die-off, 
and reducing DO), which in turn may have lethal or other harmful 
effects (prematurely aborting glochidia, reduced growth rates) to the 
species, or may cause stranding mortality.

Sedimentation

    Numerous potential sources of sand and silt sediments occur 
throughout the basin, and include development, silviculture, livestock 
grazing, croplands, and unpaved roads. Habitat may be degraded or 
destroyed in localized areas where sediments accumulate, and suspended 
fine particles can increase turbidity levels for considerable distances 
downstream. High levels of suspended sediments may reduce mussel 
feeding and respiratory efficiency (Dennis 1984, pp. 207-212; Brim Box 
and Mossa 1999, pp. 101-102). Highly turbid conditions may also affect 
mussel recruitment by impeding the ability of sight-feeding fishes to 
find glochidia and mussel lures. The Suwannee moccasinshell uses small 
mantel lures to attract its darter host fish (see Habitat and Biology 
section above) and, therefore, is reliant on good water clarity during 
times that it is reproducing. Another important issue related to 
sedimentation is that it may serve as a vehicle for pollutants (like 
pesticides and surfactants) to enter streams (Haag 2012, p. 378).
    The Suwannee River main channel is relatively unimpacted by 
sedimentation, where inputs are generally low and impacts are mostly 
localized; however, sedimentation is a problem in the Santa Fe River 
sub-basin. Surface drainage is more prevalent in the Santa Fe 
watershed, which is more developed because of its proximity to 
Gainesville, FL, and several other incorporated areas (FDEP 2003, p. 
23). Excessive silt sediment has been cited as a reason for the decline 
of mussel populations in the Santa Fe sub-basin (FFWCC 2011b, p. 14) 
and is considered a factor in the decline of the Suwannee moccasinshell 
in that system.

Conservation Efforts To Reduce Habitat Destruction, Modification, or 
Curtailment of Its Range

    We are not aware of any conservation efforts that may help 
ameliorate threats specific to the Suwannee moccasinshell. However, the 
moccasinshell may be indirectly benefited by Federal, State, local, and 
private programs that acquire or manage lands within the basin, 
particularly along stream corridors. Florida's Suwannee River Water 
Management District (SRWMD) owns, manages, or co-manages a significant 
portion of the basin's riparian lands (more than 48,000 acres, CBI 
2010) adjacent to or upstream of Suwannee moccasinshell habitats. 
Tracts are managed to maintain adequate water supply and water quality 
for natural systems by preserving riparian habitats and restricting 
development (SRWMD 2014, p. 3). The SRWMD also established minimum 
flows and levels for the river channel in the lower basin, downstream 
of Fanning Springs. Minimum flow and level criteria were not designed 
with specific consideration for freshwater mussels, but do establish a 
limit at which further withdrawals would be detrimental to water 
resources, taking into consideration fish and wildlife habitats, the 
passage of fish, sediment loads, and water quality, among others (SRWMD 
2005, pp. 6-8).

Summary of Factor A

    Habitat degradation is occurring throughout the entire range of the 
Suwannee moccasinshell and is due primarily to pollutants discharged 
from municipal and industrial facilities, polluted runoff from 
agricultural areas, and reduced flows as a result of groundwater 
pumping and drought. In portions of the species' range, sedimentation 
has also impacted the species' habitat. These threats are greater in 
the two tributary systems, as evidenced by the species' possible 
disappearance from the Withlacoochee River, and its dramatic decline in 
the Santa Fe River sub-basin. Currently, nearly the entire population 
resides in the middle and lower reach of the Suwannee River main 
channel. The two greatest threats to the species, pollutants and 
reduced flows, are somewhat attenuated in the main channel, where flows 
are generally sustained and pollutant concentrations may be diluted by 
higher flow volumes. While there are programs in place that may 
indirectly alleviate some detrimental impacts on aquatic habitats, 
there currently are no conservation efforts designed specifically to 
protect or recover Suwannee moccasinshell populations. Therefore, we 
conclude that habitat degradation is presently a significant threat to 
Suwannee moccasinshell populations in the Withlacoochee and Santa Fe 
River sub-basins, and a moderate threat to populations in the Suwannee 
River main channel. This threat is expected to continue into the future 
and, because it is linked to human activities, is expected to increase 
as the human population within the Suwannee River Basin grows.

Factor B. Overutilization for Commercial, Recreational, Scientific, or 
Educational Purposes

    The Suwannee moccasinshell is not a commercially valuable species, 
and the Suwannee River is not subject to commercial mussel harvesting 
activities. Suwannee moccasinshell individuals have been taken for 
scientific and private collections in the past, but collecting is not 
considered a factor in its decline. Collection interest may increase as 
the Suwannee moccasinshell becomes an interest of scientific study, and 
as its rarity becomes better known.

[[Page 60343]]

However, individuals are very difficult to locate because the species 
occurs in a large mainstem river in low abundance. Therefore, we do not 
consider overutilization to be a threat to the Suwannee moccasinshell 
at this time.

Factor C. Disease or Predation

    Juvenile and adult mussels are preyed upon by several aquatic 
predators (for example, dragonfly larvae, crayfishes, turtles, and some 
fishes), and are prey items for some terrestrial species (for example, 
raccoon, otter, feral hogs, and birds) (summarized in Hart and Fuller 
1974, pp. 225-240; and in Williams et al. 2014, pp. 90-91). Although 
predation by native predators is a natural occurrence, it may 
exacerbate declines in mussel populations already diminished by other 
threats (Neves and Odom 1989, p. 940). However, we have no specific 
information indicating that predation is negatively impacting Suwannee 
moccasinshell populations.
    Mussels commonly are hosts for a variety of parasites, including 
trematodes, copepods, and water mites, and also harbor bacteria and 
viruses (Grizzle and Brunner 2007, p. 4; Haag 2012, pp. 382-383). Heavy 
infestations by mites and trematodes have shown to adversely affect 
mussel reproductive and physiological fitness (Gangloff 2008, pp. 28-
30). In addition, exposure to stressors like pollutants can weaken 
mussel immune systems, making them more prone to diseases. However, the 
role of diseases in mussel declines has received little attention, and 
diseases of freshwater mussels remain largely unstudied (Grizzle and 
Bruner 2007, p. 6; Haag 2012, p. 382). We have no specific information 
indicating that disease is negatively impacting Suwannee moccasinshell 
populations. Therefore, we do not consider disease or predation to be 
threats to the Suwanee moccasinshell at this time.

Factor D. The Inadequacy of Existing Regulatory Mechanisms

    Point source discharges within the range of the Suwannee 
moccasinshell have been reduced since the inception of the Clean Water 
Act, but this statute still may not provide adequate protection for 
sensitive aquatic organisms like freshwater mussels, which can be 
impacted by extremely low levels of pollutants. Municipal wastewater 
plants continue to discharge large amounts of effluent and, in some 
circumstances, in excess of permitted levels (see discussion under 
Factor A). There is no specific information on the sensitivity of the 
Suwannee moccasinshell to common industrial and municipal pollutants, 
and very little information on other freshwater mussel species. Current 
State and Federal regulations regarding pollutants are designed to be 
protective of aquatic organisms; however, freshwater mollusks may be 
more susceptible to some pollutants than the test organisms commonly 
used in bioassays. Additionally, water quality criteria may not 
incorporate data available for freshwater mussels (March et al. 2007, 
pp. 2,066-2,067). A multitude of bioassays conducted on 16 mussel 
species (summarized by Augspurger et al. 2007, pp. 2025-2028) show that 
freshwater mollusks are more sensitive than previously known to some 
chemical pollutants, including chlorine, ammonia, copper, fungicides, 
and herbicide surfactants. Another study found that nickel and chlorine 
were toxic to a federally threatened mussel species at levels below the 
current criteria (Gibson 2015, pp. 90-91). The study also found the 
mussel was sensitive to SDS (sodium dodecyl sulfate), a surfactant 
commonly used in household detergents, for which water quality criteria 
do not currently exist.
    Several studies have demonstrated that the criteria for ammonia 
developed by EPA in 1999 were not protective of freshwater mussels 
(Augspurger et al. 2003, p. 2,571; Newton et al. 2003, pp. 2,559-2,560; 
Mummert et al. 2003, pp. 2,548-2,552). However, in 2013 EPA revised its 
recommended criteria for ammonia. The new criteria are more stringent 
and reflect new toxicity data on sensitive freshwater mollusks (78 FR 
52192, August 22, 2013; p. 2). Georgia and Florida have not yet adopted 
the new ammonia criteria. Although Florida's next triennial review will 
occur in 2015 and Georgia's in 2016, NPDES permits are valid for 5 
years, so even after the new criteria are adopted, it could take 
several years before facilities must comply with the new limits.
    In summary, despite existing authorities such as the Clean Water 
Act, pollutants continue to impair the water quality throughout the 
current range of the Suwannee moccasinshell. State and Federal 
regulatory mechanisms have helped reduce the negative effects of point 
source discharges since the 1970s, yet these regulations are difficult 
to implement and regulate. While new water quality criteria are being 
developed that take into account more sensitive aquatic species, most 
criteria currently do not. Thus, we conclude that existing regulatory 
mechanisms do not adequately protect the Suwannee moccasinshell.

Factor E. Other Natural or Manmade Factors Affecting Its Continued 
Existence

Catastrophic Weather Events
    The Gulf coastal region is prone to extreme hydrologic events. 
Extended droughts result from persistent high-pressure systems, which 
inhibit moisture from the Gulf of Mexico from reaching the region 
(Jeffcoat et al. 1991, pp. 163-170). Warm, humid air from the Gulf of 
Mexico can produce strong frontal systems and tropical storms resulting 
in heavy rainfall events that cause severe flooding (Jeffcoat et al. 
1991, pp. 163-170). Although floods and droughts are a natural part of 
the hydrologic processes that occur in these river systems, these 
events may exacerbate the decline of mussel populations suffering the 
effects of other threats. During high flows, flood scour can dislodge 
mussels (particularly juveniles) where they may be injured, buried, or 
swept into unsuitable habitats, or mussels may be stranded and perish 
when flood waters recede (Vannote and Minshall 1982, p. 4,105; Tucker 
1996, p. 435; Hastie et al. 2001, pp. 107-115; Peterson et al. 2011, 
unpaginated). Flood scour generally is attenuated in larger stream 
channels but can radically alter smaller streams and cause mussel 
mortality (Hastie et al. 2001, pp. 107-115; Peterson et al. 2011, 
unpaginated).
    During drought, stream channels may be dewatered entirely, or 
become disconnected pools where mussels are exposed to higher water 
temperatures, lower dissolved oxygen levels, and predators. Johnson et 
al. (2001, p. 6) monitored mussel responses during a severe drought in 
2000 in tributaries of the lower Flint River in Georgia, and found that 
most mortality occurred when dissolved oxygen levels dropped below 5 
mg/L. Increased demand for surface and ground water resources for 
irrigation and human consumption during drought can cause drastic 
reductions in stream flows and alterations to hydrology (Golladay et 
al. 2004, p. 504; Golladay et al. 2007 unpaginated). Extended periods 
of drought have occurred in the region during the last two decades 
(Torak et al. 2010, p. 47). Substantial declines in mussel diversity 
and abundance as a direct result of drought have been documented in 
smaller southeastern streams; however, assemblages in larger streams 
may be relatively unaffected (Golladay et al. 2004, pp. 494-503; Haag 
and Warren 2008, p. 1165). Reduced flows as a result of drought and 
water consumption has been cited as a factor negatively affecting 
mussels in the

[[Page 60344]]

Suwannee River Basin (FFWCC 2011b, p. 14), and has been identified as a 
threat to Suwannee moccasinshell populations in the Withlacoochee and 
Santa Fe Rivers (Williams 2015, p. 9)

Contaminant Spills

    The linear nature of the Suwannee moccasinshell's habitat and its 
reduced range makes it vulnerable to contaminant spills. Spills as a 
result of transportation accidents are a constant potential threat to 
the species, as numerous highways and railroads traverse the basin. 
Spills emanating from industrial, agricultural, and municipal 
facilities are a threat as numerous potential sources are present 
within the basin, and these spills have occurred in the past. As 
discussed under Factor A, spills at the municipal WWTP in Valdosta, GA, 
have leaked raw sewage into the Withlacoochee River on multiple 
occasions, and the PCS Phosphate Company, Inc. mining operation has had 
periodic overflows of effluent ponds. Nearly the entire moccasinshell 
population resides within the Suwannee River main channel; therefore, a 
spill has the potential to impact a large portion of the population, 
depending on the type of contaminant and its concentration, amount, and 
location. In addition, because the species has limited ability to 
disperse, it may not be able recolonize areas after conditions have 
improved.

Climate Change

    Our analyses under the Act include consideration of ongoing and 
projected changes in climate. The terms ``climate'' and ``climate 
change'' are defined by the Intergovernmental Panel on Climate Change 
(IPCC). ``Climate'' refers to the mean and variability of different 
types of weather conditions over time, with 30 years being a typical 
period for such measurements, although shorter or longer periods also 
may be used (IPCC 2007, p. 78). The term ``climate change'' thus refers 
to a change in the mean or variability of one or more measures of 
climate (e.g., temperature or precipitation) that persists for an 
extended period, typically decades or longer, whether the change is due 
to natural variability, human activity, or both (IPCC 2007, p. 78). 
Various types of changes in climate can have direct or indirect effects 
on species. These effects may be positive, neutral, or negative and 
they may change over time, depending on the species and other relevant 
considerations, such as the effects of interactions of climate with 
other variables (e.g., habitat fragmentation) (IPCC 2007, pp. 8-14, 18-
19). In our analyses, we use our expert judgment to weigh relevant 
information, including uncertainty, in our consideration of various 
aspects of climate change.
    There is a growing concern that climate change may lead to 
increased frequency of severe storms and droughts (McLaughlin et al. 
2002, p. 6,074; Golladay et al. 2004, p. 504; Cook et al. 2004, p. 
1,015). The present conservation status, complex life histories, and 
specific habitat requirements of freshwater mussels suggest that they 
may be quite sensitive to climate change (Hastie et al. 2003, p. 45). 
Specific effects of climate change to mussels, their habitat, and their 
fish hosts could include changes in hydrologic and temperature regimes, 
the timing and levels of precipitation causing more frequent and severe 
floods and droughts, and alien species introductions.
    Mussel distributions seem to be closely associated with complex 
hydraulic metrics (Morales et al. 2006 pp. 669-673; Zigler et al. 2008, 
p. 358) that may be altered by climate change. Mussels are particularly 
vulnerable to these changes since they are generally sessile and 
restricted in their ability to adjust their range in response to 
hydrology and physiochemical alterations mediated by climate change 
(Strayer 2008, p. 30). Additionally, increases in temperature and 
reductions in flow may lower dissolved oxygen levels in interstitial 
habitats, which can be lethal to juveniles (Sparks and Strayer 1998, 
pp. 131-133). Effects to mussel populations from these environmental 
changes could include reduced abundance and biomass, altered species 
composition, and host fish considerations (Galbraith et al. 2010, pp. 
1,180-1,182). Since ammonia concentrations may increase with increasing 
temperatures and low stream flow (Cherry et al. 2005, p. 378; Cooper et 
al. 2005, p. 381), nitrogen-mediated threats may be intensified by 
climate change. In addition, saltwater encroachment, as a result of 
rising sea levels, has the potential to impact freshwater habitats in 
the lower reaches of coastal rivers.
    Long-term sea level trends available from the Cedar Key tide gage 
suggest the local sea level is rising about 1.8 mm (0.7 inches) per 
year based on data from 1914 to 2006 (Thom et al. 2015, pp. 47-48). At 
this rate, this is equivalent to 0.14 meters (0.46 feet) by 2100. 
However, all indications are that sea level rise (SLR) is accelerating 
(Thom et al. 2015, p. 47), and, although there is a range of estimates, 
recent studies suggest that global mean sea level will rise at least 
0.2 meters (0.66 ft) and no more than 2.0 meters (6.6 ft) by 2100 
(Parris et al. 2012, pp. 1-2).
    The effects of climate change may amplify stressors currently 
impacting the Suwannee moccasinshell, including the prospect of more 
frequent and intense droughts and increased temperatures, which would 
further reduce flows, increase pollutant toxicity levels, and 
exacerbate current problems of low DO and excessive algae growth (see 
discussions under Factor A). Saltwater encroachment also has the 
potential to impact moccasinshell populations in the lower river, 
especially during times of low flow conditions. The variables related 
to climate change are complex, and it is difficult to predict all of 
the possible ways climate change will affect Suwannee moccasinshell 
populations and habitat. However, information available is sufficient 
to indicate that climate change is a significant threat to the Suwannee 
moccasinshell in the future, as it will likely exacerbate certain 
stressors already affecting the species, such as reduced flows and 
degraded water quality.

Small Population Size

    The Suwannee moccasinshell's reduced range and small population 
size may increase its vulnerability to many threats. Species with small 
ranges, few populations, and small or declining population sizes are 
the most vulnerable to extinction (Primack 2008, p. 137). The effects 
of certain environmental pressures, particularly habitat degradation 
and loss, catastrophic weather events, and introduced species, are 
greater when population size is small (Soul[eacute] 1980, pp. 33, 71; 
Primack 2008, pp. 133-137, 152). Suwannee moccasinshell populations are 
small and declining and are vulnerable to habitat degradation, 
droughts, and competition from the introduced Asian clam. In addition, 
its current range is relatively small, consisting of a stream channel 
segment of about 103 miles in length (see Distribution and Abundance 
discussion).

Nonindigenous Species

    The Asian clam (Corbicula fluminea) was first detected in eastern 
Gulf drainages in the early 1960s and is presently widespread in the 
Suwannee River Basin. Anecdotal observations suggest that, when the 
Asian clam became established in other Gulf coast drainages, native 
mussel abundance declined drastically (Heard 1975, p. 2; Shelton 1995, 
p. 4). It is unknown, however, if the Asian clam competitively excluded 
the native mussels, are tolerant of whatever caused

[[Page 60345]]

them to disappear, or, as Haag (2012, p. 371) suggests, the Asian clam 
is a poor competitor and can only become dense after a decline in 
mussel abundance. Mechanisms by which the Asian clam may negatively 
affect mussels include as a competitor for food and space; by ingesting 
mussel sperm, glochidia, and newly metamorphosed juveniles; and by 
displacing newly metamorphosed mussels from the substrate, causing them 
to be washed downstream (Neves and Widlak 1987, p. 6; Leff et al. 1990, 
p. 415; Strayer 1999, p. 82; Yeager et al. 2000, pp. 255-257). Although 
the specific interaction between the Asian clam and native mussels is 
not well understood, enough information exists to conclude that dense 
Asian clam populations would negatively affect juvenile mussel survival 
(Haag 2012, p. 370). Surveys within the range of the Suwannee 
moccasinshell found Asian clam densities varied from relatively low in 
some areas to relatively high in other areas (S. Pursifull 2014 pers. 
obs.). The introduced Asian clam is negatively affecting the Suwannee 
moccasinshell, although we consider this threat to be low at present.
    The flathead catfish (Pylodictis olivaris) has been introduced to 
the Suwannee River Basin and may be adversely impacting native fish 
populations. As discussed in the Habitat and Biology section above, the 
Suwannee moccasinshell requires a fish host in order to complete its 
life cycle, and the blackbanded darter and the brown darter were found 
to serve as larval hosts for the moccasinshell. The flathead catfish is 
a large predator native to the central United States, and since its 
introduction outside its native range, it has altered the composition 
of native fish populations through predation (Boschung and Mayden 2004, 
p. 350). Many feeding studies have found that flathead catfish prey 
heavily on other fishes, especially sunfishes (Centrarchidae) (Weller 
and Robbins 1999, p. 40; Pine et al. 2005, p. 904). One study in the 
Flint River system in Georgia found that young-of-the-year flatheads 
consumed several fish species including darters (Etheostoma spp.) 
(Quinn 1988, p. 88). The loss or reduction of darters, which are 
essential during the moccasinshell's parasitic larval stage, would 
affect the Suwannee moccasinshell's ability to recruit and disperse. 
However, it is not known if the specific darter species needed by this 
mussel to reproduce are being predated by introduced flatheads; 
therefore, it is difficult for us to evaluate this potential threat at 
this time.
    In summary, the Suwannee moccasinshell is adversely affected by 
other natural or manmade factors including droughts that (along with 
groundwater consumption) cause reduced flows, past and future 
contaminant spills, and the introduced Asian clam. In addition, 
numerous future impacts associated with changing climatic patterns 
(increased drought frequency, altered water quality, saltwater 
encroachment) are anticipated, some of which could intensify stressors 
currently affecting the species, including reduced flows and low DO. 
For this reason, problems related to reduced flows and degraded water 
quality are expected to increase in the future. Finally, the Suwannee 
moccasinshell's small population size and restricted range makes it 
more vulnerable to certain threats. Therefore, we find that these 
threats, as a whole, pose a significant threat to the Suwannee 
moccasinshell, both now and continuing into the future. The Suwannee 
moccasinshell may also be affected by flood events, and predation of 
its host fishes by introduced flathead catfish. However, we do not have 
information indicating that these are currently acting on the species 
at this time.

Proposed Determination

    We have carefully assessed the best scientific and commercial 
information available regarding the past, present, and future threats 
to the Suwannee moccasinshell. The primary reason for the Suwannee 
moccasinshell's decline is the degradation of its habitat due to 
polluted runoff from agricultural lands, discharges from industrial and 
municipal wastewater sources and from mining operations, and decreased 
flows due to groundwater extraction and drought (Factor A). These 
threats occur throughout its range, but are more intense in the two 
tributaries, the Withlacoochee and Santa Fe River systems. In portions 
of its range, sedimentation has also impacted its habitat. Other 
threats to the species include State and Federal water quality 
standards that are inadequate to protect sensitive aquatic organisms 
like mussels (Factor D); contaminant spills as a result of 
transportation accidents or from industrial, agricultural, and 
municipal facilities (Factor E); increased drought frequency as a 
result of changing climatic conditions (Factor E); greater 
vulnerability to certain threats because of small population size and 
range (Factor E); and competition and disturbance from the introduced 
Asian clam (Factor E). These threats have resulted in the decline of 
the species throughout its range, and pose the highest risk to 
populations in the two tributary systems, as evidenced by the species' 
decline and possible disappearance in the Withlacoochee River, and its 
decline in the Santa Fe River sub-basin. In addition, the species 
likely has a limited ability to disperse and, therefore, may not be 
able recolonize areas from which it has been extirpated. Currently, 
nearly the entire population resides in the middle and lower reach of 
the Suwannee River main channel, where the two greatest threats, 
pollutants and reduced flows, are attenuated by higher flow volumes. 
Therefore, Suwannee moccasinshell populations in the Withlacoochee and 
Santa Fe River sub-basins are presently facing threats that are high in 
magnitude, and populations in the Suwannee River main channel are 
presently facing threats that are moderate in magnitude. Most of these 
threats, including reduced flows, pollutants, droughts, and climate 
change, are expected to increase in the future.
    The Act defines an endangered species as any species that is ``in 
danger of extinction throughout all or a significant portion of its 
range'' and 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 Suwannee 
moccasinshell is likely to become endangered throughout all or a 
significant portion of its range within the foreseeable future based on 
the overall severity and immediacy of threats currently impacting the 
species. The Suwannee moccasinshell's range and abundance have been 
reduced, and its remaining habitat and populations are threatened by a 
variety of factors acting in combination to reduce the overall 
viability of the species. The risk of becoming endangered is high 
because remaining Suwannee moccasinshell populations in the main 
channel are small and numerous threats impact those populations. 
However, we find that endangered species status is not appropriate, 
because despite low population densities and numerous threats, the 
populations in the main channel, which are the largest, appear to be 
stable, which has been attributed to the threats being attenuated and 
the streambed habitat being stable. Therefore, on the basis of the best 
available scientific and commercial information, we propose listing the 
Suwannee moccasinshell as threatened in accordance with sections 3(6) 
and 4(a)(1) of the Act.

[[Page 60346]]

Significant Portion of the Range

    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 
Suwannee moccasinshell is threatened throughout all of its range, no 
portion of its range can be ``significant'' for purposes of the 
definitions of ``endangered species'' and ``threatened species.'' See 
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 37578; July 1, 
2014).

Critical Habitat

    Section 3(5)(A) of the Act defines critical habitat as (i) the 
specific areas within the geographical area occupied by the species, at 
the time it is listed on which are found those physical or biological 
features (I) essential to the conservation of the species and (II) 
which may require special management considerations or protection; and 
(ii) specific areas outside the geographical area occupied by the 
species at the time it is listed upon a determination by the Secretary 
that such areas are essential for the conservation of the species. 
Section 3(3) of the Act (16 U.S.C. 1532(3)) also defines the terms 
``conserve,'' ``conserving,'' and ``conservation'' to mean to use and 
the use of all methods and procedures which are necessary to bring any 
endangered species or threatened species to the point at which the 
measures provided pursuant to this chapter Act are no longer necessary.
    Section 4(a)(3) of the Act, as amended, and implementing 
regulations (50 CFR 424.12), require that, to the maximum extent 
prudent and determinable, the Secretary shall designate critical 
habitat at the time the species is determined to be an endangered or 
threatened species. Our regulations in title 50 of the Code of Federal 
Regulations (50 CFR 424.12(a)(1)) state that the designation of 
critical habitat is not prudent when one or both of the following 
situations exist:
    (1) The species is threatened by taking or other human activity, 
and identification of critical habitat can be expected to increase the 
degree of threat to the species, or
    (2) Such designation of critical habitat would not be beneficial to 
the species.
    There is currently no imminent threat of take attributed to 
collection or vandalism under Factor B for this species, and 
identification and mapping of critical habitat is not expected to 
initiate any such threat. In the absence of finding that the 
designation of critical habitat would increase threats to a species, if 
there are any benefits to a critical habitat designation, a finding 
that designation is prudent is warranted. Here, the potential benefits 
of designation include: (1) Triggering consultation under section 7 of 
the Act, in new areas for actions in which there may be a Federal nexus 
where it would not otherwise occur because, for example, it is 
unoccupied; (2) focusing conservation activities on the most essential 
features and areas; (3) providing educational benefits to State or 
county governments or private entities; and (4) preventing people from 
causing inadvertent harm to the species.
    Because we have determined that the designation of critical habitat 
will not likely increase the degree of threat to the species and may 
provide some measure of benefit, we determine that designation of 
critical habitat is prudent for the Suwannee moccasinshell.
    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.
    Delineation of critical habitat requires, within the geographical 
area occupied by the Suwannee moccasinshell, identification of the 
physical or biological features essential to the conservation of the 
subspecies. While we have significant information on the habitat of the 
species, we need more information on biological needs of the species 
(i.e., specific habitat features on the landscape) in order to identify 
specific areas appropriate for critical habitat designation. In 
addition, as we have not determined the areas that may qualify for 
designation, the information sufficient to perform a required analysis 
of the impacts of the designation is lacking. Accordingly, we find 
designation of critical habitat to be not determinable at this time.

Available Conservation Measures

    Conservation measures provided to species listed as endangered or 
threatened 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 or delisting, 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. If this 
species is listed as proposed, a recovery outline, draft recovery plan, 
and the final recovery plan would be made available on our Web site 
(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

[[Page 60347]]

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 range 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 States of Florida and Georgia 
would be eligible for Federal funds to implement management actions 
that promote the protection or recovery of the Suwannee moccasinshell. 
Information on our grant programs that are available to aid species 
recovery can be found at: http://www.fws.gov/grants.
    Although the Suwannee moccasinshell is only proposed for listing 
under the Act at this time, please let us know if you are interested in 
participating in conservation 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 conservation 
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 Service and the U.S. 
Department of Agriculture's (USDA) U.S. Forest Service; issuance of 
section 404 Clean Water Act permits by the U.S. Army Corps of 
Engineers; construction and maintenance of roads, highways, or bridges 
by the U.S. Department of Transportation's Federal Highway 
Administration; and funding assistance for various projects 
administered by USDA's Natural Resources Conservation Service and the 
Federal Emergency Management Agency.
    Under section 4(d) of the Act, the Service has discretion to issue 
regulations that we find necessary and advisable to provide for the 
conservation of threatened species. 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 Oceanic and Atmospheric Administration's 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 and for incidental take in connection with otherwise lawful 
activities. 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 the effect of a proposed 
listing on proposed and ongoing activities within the range of species 
proposed for listing. Based on the best available information, the 
following activities may potentially result in a violation of section 9 
the Act; this list is not comprehensive:
    Activities that the Service believes could potentially harm the 
Suwannee moccasinshell 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 discharge 
of fill material, dredging, snagging, impounding, channelization, or 
modification of stream channels or banks;
    (3) Discharge of pollutants into a stream or into areas 
hydrologically connected to a stream occupied by the species; and
    (4) Diversion or alteration of surface or ground water flow.
    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).

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

[[Page 60348]]

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 
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 this rulemaking 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).

Authors

    The primary authors of this proposed rule are the staff members of 
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--[AMENDED]

0
1. The authority citation for part 17 continues to read as follows:

    Authority: 16 U.S.C. 1361-1407; 1531-1544; 4201-4245; unless 
otherwise noted.

0
2. In Sec.  17.11(h), add an entry for ``Moccasinshell, Suwannee'' to 
the List of Endangered and Threatened Wildlife in alphabetical order 
under CLAMS to read as set forth below:


Sec.  17.11  Endangered and threatened wildlife.

* * * * *
    (h) * * *

--------------------------------------------------------------------------------------------------------------------------------------------------------
                        Species                                                    Vertebrate
--------------------------------------------------------                        population where                                  Critical     Special
                                                            Historic range       endangered or         Status      When listed    habitat       rules
           Common name                Scientific name                              threatened
--------------------------------------------------------------------------------------------------------------------------------------------------------
 
                                                                      * * * * * * *
              Clams
 
                                                                      * * * * * * *
Moccasinshell, Suwannee..........  Medionidus walkeri..  U.S.A. (FL, GA)....  NA.................  T                        XX           NA           NA
 
                                                                      * * * * * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------

* * * * *

    Dated: September 9, 2015.
Stephen Guertin,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2015-25280 Filed 10-5-15; 8:45 am]
 BILLING CODE 4310-55-P