Endangered and Threatened Wildlife and Plants; Threatened Species Status for Platanthera integrilabia (White Fringeless Orchid), 62826-62833 [2016-21954]
Download as PDF
62826
*
*
Federal Register / Vol. 81, No. 177 / Tuesday, September 13, 2016 / Rules and Regulations
*
*
*
DATES:
This rule is effective October 13,
[FR Doc. 2016–21637 Filed 9–12–16; 8:45 am]
BILLING CODE 6712–01–P
Background
2016.
This final rule is available
on the Internet at https://
www.regulations.gov and https://
www.fws.gov/cookeville. Comments and
materials we received, as well as
supporting documentation we used in
preparing this rule, are available for
public inspection at https://
www.regulations.gov, or by
appointment, during normal business
hours, at: U.S. Fish and Wildlife
Service, Tennessee Ecological Services
Field Office, 446 Neal Street,
Cookeville, TN 38501; telephone: 931–
528–6481; facsimile: 931–528–7075.
FOR FURTHER INFORMATION CONTACT:
Mary Jennings, Field Supervisor, U.S.
Fish and Wildlife Service, Tennessee
Ecological Services Field Office (see
ADDRESSES, above). Persons who use a
telecommunications device for the deaf
(TDD) may call the Federal Information
Relay Service (FIRS) at 800–877–8339.
SUPPLEMENTARY INFORMATION:
Below, we update and summarize
information from the proposed listing
rule for the white fringeless orchid (80
FR 55304; September 15, 2015) on the
historical and current distribution of
white fringeless orchid. Please refer to
the proposed listing rule for a summary
of other species information, including
habitat, biology, and genetics.
ADDRESSES:
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–R4–ES–2015–0129;
4500030113]
RIN 1018–BA93
Endangered and Threatened Wildlife
and Plants; Threatened Species Status
for Platanthera integrilabia (White
Fringeless Orchid)
Fish and Wildlife Service,
Interior.
ACTION: Final rule.
AGENCY:
We, the U.S. Fish and
Wildlife Service (Service), determine
threatened species status under the
Endangered Species Act of 1973 (Act),
as amended, for Platanthera integrilabia
(white fringeless orchid), a plant species
from Alabama, Georgia, Kentucky,
Mississippi, South Carolina, and
Tennessee. This rule adds this species
to the Federal List of Endangered and
Threatened Plants.
SUMMARY:
Distribution
In this final rule, we are updating
information on the species’ distribution
from the September 15, 2015, proposed
rule to include two minor changes,
which were brought to our attention
following publication of the proposed
listing rule. First, we are changing the
2014 status of the Forsyth County,
Georgia, population from extant to
uncertain (Table 1), because flowering
plants have not been documented at this
site since 1990 (Richards 2015, pers.
comm.). In addition, we have added
Georgia Department of Transportation
(GDOT) to the list of local, State, or
Federal government entities that own or
manage lands where white fringeless
orchid is present (Table 2). A revised
summary of the species’ distribution
follows.
Previous Federal Actions
Please refer to the proposed listing
rule for the white fringeless orchid (80
FR 55304; September 15, 2015) for a
detailed description of previous Federal
actions concerning this species.
TABLE 1—COUNTY-LEVEL DISTRIBUTION OF EXTANT AND UNCERTAIN STATUS WHITE FRINGELESS ORCHID OCCURRENCES, CIRCA 1991 (SHEA 1992) AND 2014 (ANHP 2014, GDNR 2014, KSNPC 2014, MDWFP 2014, NCDENR
2014, SCDNR 2012, SCHOTZ 2015, AND TDEC 2014)
1991
State
2014
County
Extant
Alabama ............................................
Georgia .............................................
Kentucky ...........................................
Lhorne on DSK30JT082PROD with RULES
Mississippi .........................................
South Carolina ..................................
Tennessee ........................................
VerDate Sep<11>2014
15:24 Sep 12, 2016
Calhoun ............................................
Clay ..................................................
Cleburne ...........................................
DeKalb ..............................................
Jackson ............................................
Marion ..............................................
Tuscaloosa .......................................
Winston ............................................
Bartow ..............................................
Carroll ...............................................
Chattooga .........................................
Cobb .................................................
Coweta .............................................
Forsyth .............................................
Pickens .............................................
Rabun ...............................................
Stephens ..........................................
Laurel ...............................................
McCreary ..........................................
Pulaski ..............................................
Whitley ..............................................
Alcorn ...............................................
Itawamba ..........................................
Tishomingo .......................................
Greenville .........................................
Bledsoe ............................................
Cumberland ......................................
Fentress ...........................................
Franklin .............................................
Jkt 238001
PO 00000
Frm 00018
Fmt 4700
Uncertain
Extant
Uncertain
........................
........................
........................
........................
........................
1
1
1
........................
2
........................
1
1
........................
........................
1
1
........................
4
1
........................
........................
........................
........................
1
........................
........................
........................
3
........................
1
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
........................
1
........................
........................
........................
........................
........................
1
........................
........................
........................
........................
........................
2
........................
........................
2
2
1
1
1
........................
1
1
1
1
2
1
........................
1
........................
1
1
1
2
2
2
1
........................
2
1
........................
2
1
2
5
........................
........................
........................
........................
1
2
........................
........................
........................
........................
........................
........................
........................
1
........................
........................
........................
2
1
........................
........................
1
1
1
1
1
........................
........................
5
Sfmt 4700
E:\FR\FM\13SER1.SGM
13SER1
Federal Register / Vol. 81, No. 177 / Tuesday, September 13, 2016 / Rules and Regulations
62827
TABLE 1—COUNTY-LEVEL DISTRIBUTION OF EXTANT AND UNCERTAIN STATUS WHITE FRINGELESS ORCHID OCCURRENCES, CIRCA 1991 (SHEA 1992) AND 2014 (ANHP 2014, GDNR 2014, KSNPC 2014, MDWFP 2014, NCDENR
2014, SCDNR 2012, SCHOTZ 2015, AND TDEC 2014)—Continued
1991
State
2014
County
Extant
Grundy ..............................................
Marion ..............................................
McMinn .............................................
Polk ..................................................
Scott .................................................
Sequatchie .......................................
Van Buren ........................................
Total ...........................................
Uncertain
Extant
Uncertain
5
2
1
........................
........................
2
2
5
........................
........................
........................
........................
1
........................
4
8
1
1
1
1
5
4
........................
........................
........................
........................
1
1
...........................................................
30
13
57
23
TABLE 2—STATUS AND NUMBER OF WHITE FRINGELESS ORCHID OCCURRENCES ON PUBLICLY OWNED OR MANAGED
LANDS
[Note: One site is on privately owned lands that the Georgia Department of Natural Resources (GDNR) leases for use as a wildlife management
area]
Ownership
Extant
Uncertain
Extirpated
Historical
National Park Service ......................................................................................
U.S. Forest Service .........................................................................................
U.S. Fish and Wildlife Service .........................................................................
Alabama Department of Conservation and Natural Resources ......................
Georgia Department of Natural Resources .....................................................
Georgia Department of Transportation ............................................................
Kentucky State Nature Preserves Commission ..............................................
Mississippi Department of Fish, Wildlife, and Parks .......................................
North Carolina Plant Conservation Program ...................................................
South Carolina State Parks .............................................................................
Tennessee Department of Transportation .......................................................
Tennessee Division of Forestry .......................................................................
Tennessee State Parks ...................................................................................
Tennessee Wildlife Resources Agency ...........................................................
Forsyth County, Georgia .................................................................................
3
9
2
........................
2
1
1
1
........................
........................
1
7
5
1
........................
........................
3
........................
1
........................
........................
........................
........................
........................
1
........................
........................
1
........................
1
........................
3
........................
........................
........................
........................
........................
........................
1
........................
........................
........................
........................
1
........................
........................
........................
........................
........................
........................
........................
1
........................
........................
........................
........................
........................
1
........................
........................
Total ..........................................................................................................
33
7
5
2
Lhorne on DSK30JT082PROD with RULES
All other information from the
‘‘Distribution’’ discussion in the
proposed rule (80 FR 55304; September
15, 2015) remains unchanged.
Summary of Comments and
Recommendations
In the proposed rule published on
September 15, 2015 (80 FR 55304), we
requested that all interested parties
submit written comments on the
proposal by November 16, 2015. We
also contacted appropriate Federal and
State agencies, scientific experts and
organizations, and other interested
parties and invited them to comment on
the proposal. On April 14, 2016 (81 FR
22041), we reopened the comment
period for an additional 60 days, ending
June 13, 2016. Newspaper notices
inviting general public comment were
published in the Asheville Citizen
Times, Birmingham News, Chattanooga
Times Free Press, Greenville News,
Huntsville News, Knoxville News,
Lexington Herald-Leader, and Northeast
Mississippi Daily Journal. We did not
VerDate Sep<11>2014
15:24 Sep 12, 2016
Jkt 238001
receive any requests for a public
hearing.
Peer Reviewer Comments
In accordance with our peer review
policy published on July 1, 1994 (59 FR
34270), we solicited expert opinion
from three knowledgeable individuals
with scientific expertise that included
familiarity with white fringeless orchid
and its habitat, biological needs, and
threats or general conservation biology
of orchids. We received responses from
two of the peer reviewers. We reviewed
all comments we received from the peer
reviewers for substantive issues and
new information regarding the listing of
white fringeless orchid. The peer
reviewers generally concurred with our
evaluation and the conclusion we
reached regarding the proposal to list
the white fringeless orchid as a
threatened species. One peer reviewer
commented on the information on the
species’ habitat, biology, and threats,
and provided minor updates regarding
the status and distribution of white
PO 00000
Frm 00019
Fmt 4700
Sfmt 4700
fringeless orchid in the State of Georgia.
Peer reviewer comments are addressed
in the following summary and
incorporated into the final rule as
appropriate.
(1) Comment: One reviewer
commented on subtle differences in
descriptions of white fringeless orchid
habitat that have been recorded over
time, suggesting that descriptions from
the 1970s (Luer 1975, p. 186; Shea 1992,
p. 19) or later might represent altered
conditions, as compared to the earliest
published habitat description (Correll
1941, pp. 156–157). This reviewer noted
that Correll (1941, pp. 156–157) used
the term ‘‘grassy,’’ citing an herbarium
specimen label, in describing the
habitat, possibly implying the presence
of more open conditions in which a
grassy herbaceous community would
have been present. This reviewer
speculated that the shaded, forested
conditions, discussed in more
contemporary descriptions of white
fringeless orchid habitat, might have
E:\FR\FM\13SER1.SGM
13SER1
Lhorne on DSK30JT082PROD with RULES
62828
Federal Register / Vol. 81, No. 177 / Tuesday, September 13, 2016 / Rules and Regulations
resulted from land use and regulatory
changes (i.e., regulation of impacts to
wetlands) that have favored the
development of more densely stocked,
heavily shaded contemporary forest
conditions in habitats where the white
fringeless orchid occurs. This reviewer
opined that current habitat conditions
where the white fringeless orchid occurs
do not, in many cases, represent the
optimal range of habitat variation for the
species. This reviewer also cited shortterm positive responses of white
fringeless orchid populations to timber
removal in adjacent uplands, a
phenomenon that we discussed in the
proposed listing rule, as evidence of the
positive influences of increased light
and water availability, but which
diminish with regrowth of even-aged
hardwood stands in the absence of
ecological disturbance, such as fire. One
commenter also suggested that fire
could be a beneficial management tool
in conservation efforts for the white
fringeless orchid.
Our Response: We agree with the peer
reviewer’s observations about the
potential beneficial effects of ecological
disturbance, such as fire, in creating
environmental conditions that stimulate
population growth and increased flower
production in the white fringeless
orchid. The proposed listing rule (80 FR
55304; September 15, 2015) discusses
short-term positive responses to timber
harvesting that have been observed in
some white fringeless orchid
populations and notes that Schotz
(2015, p. 4) suggested that fire could
play a role in regulating woody
vegetation growth in uplands
surrounding white fringeless orchid
habitats. The proposed rule also reports
on Hoy’s (2012, p. 26) suggestion that
high stem densities, which resulted
from succession following canopy
removal, shortened the hydroperiod of
wetlands at a white fringeless orchid
site in Kentucky. Evaluating the
potential role of fire or other ecological
disturbance in managing habitat for the
white fringeless orchid will be
considered during preparation of a
recovery plan (see discussion about
recovery plans under the heading
Available Conservation Measures,
below) for the species after it is listed.
(2) Comment: One peer reviewer
commented that the use of herbicides on
industrial and small-scale timber
operations appears to be increasing
significantly in the State of Georgia and
that we should include it as a threat of
significant concern not only to the white
fringeless orchid but also to the
herbaceous plant community of which it
is part, as well as pollinators. The
VerDate Sep<11>2014
15:24 Sep 12, 2016
Jkt 238001
reviewer did not provide specific data
in support of this comment.
Our Response: We agree that
increased use of herbicides in timber
operations in or near habitats where the
white fringeless orchid occurs could be
detrimental to the species, as well as
other herbaceous plants and pollinators,
but we are not aware of specific
instances where adverse effects to the
white fringeless orchid have occurred
due to herbicide use in silvicultural
operations, nor do we have data
regarding the rates at which herbicides
are used in silvicultural operations
presently or in the past. Therefore, we
have not added a discussion of
herbicide use in silvicultural operations
in the analysis of factors affecting the
white fringeless orchid.
(3) Comment: One peer reviewer
commented that Atlanta Botanical
Garden (ABG) has developed asymbiotic
(in the absence of symbiotic fungi),
aseptic (free from contamination caused
by harmful bacteria, viruses, or other
microorganisms) in vitro propagation
protocols that achieve much higher
germination rates than the rate (less
than 3 percent) observed by other
researchers in separate studies of in
vitro and in situ seedling development
(Zettler and McInnis 1992, pp. 157–160;
Zettler 1994, p. 65).
Our Response: The Service is aware of
the success that ABG has achieved in
propagating the white fringeless orchid;
however, we are not aware of specific
rates of seedling germination that we
can include in this rule. Effective
propagation protocols could be a
valuable tool, combined with sciencebased habitat management practices, for
augmenting currently small populations
or restoring populations in sites where
the species is no longer extant but
suitable habitat conditions remain. We
will consider this information during
development of a recovery plan for the
species.
(4) Comment: One peer reviewer
commented on the discussion in the
proposed listing rule about rates of fruit
set in relation to population size, which
cited Zettler et al. (1996, p. 22) and
Zettler and McInnis (1992, p. 160) in
suggesting that inbreeding depression
could be a cause for the lower fruit set
observed in smaller populations. The
peer reviewer commented that low
census numbers of flowering
individuals and highly fragmented or
degraded pollinator networks also could
influence the low rates observed in
smaller populations.
Our Response: We agree with the peer
reviewer that other factors besides
inbreeding depression, caused by
increased rates of self-pollination, could
PO 00000
Frm 00020
Fmt 4700
Sfmt 4700
contribute to low rates of fruit set in
small populations of the white
fringeless orchid. However, we are not
aware of specific data that indicate what
those other factors might be.
Federal Agency Comments
(5) Comment: The Tennessee Valley
Authority (TVA) commented that nearly
20 percent of extant white fringeless
orchid occurrences are located in
transportation or utility rights-of-way,
illustrating that the species occurs in
these settings at a disproportionately
high rate when compared to their
overall prevalence on the landscape.
The TVA also commented that the
proposed rule highlights the beneficial
role that vegetation maintenance, if
properly conducted, can play in
maintaining suitable habitat for the
white fringeless orchid and that
herbicide resistance in the species
could, in part, explain the positive
response seen in one population
following herbicide application in a
TVA right-of-way.
Our Response: We acknowledge that
current distribution data indicate that
the white fringeless orchid occurs in
transportation or utility rights-of-way at
a disproportionately high rate compared
to the overall prevalence of these
features on the landscape. One possible
cause for the disproportionally high
numbers of populations known from
rights-of-way is that these areas are
surveyed by TVA and other utility or
transportation departments more
frequently or intensively than the
forested habitats where most
populations are located. It might also be
true that white fringeless orchid
populations respond positively to the
well-lit conditions found in rights-ofway, assuming that other threats related
to maintenance or unauthorized use of
rights-of-way (e.g., off-road vehicle use)
do not adversely affect the plants or
their habitat. We commend TVA on its
efforts to prevent adverse effects to rare
species while conducting vegetation
management or infrastructure
maintenance in rights-of-way.
Regarding the comment that herbicide
resistance could explain the species’
positive response to selective herbicide
application, we are not aware of any
data to support the assertion that the
species is resistant to any registered
herbicide products. It is possible that
the selective nature of herbicide
application to woody species by TVA or
its contractors, rather than herbicide
resistance generally, is responsible for
the positive response seen following one
known instance of potential exposure in
a TVA right-of-way. This warrants
further research.
E:\FR\FM\13SER1.SGM
13SER1
Federal Register / Vol. 81, No. 177 / Tuesday, September 13, 2016 / Rules and Regulations
Comments From States
(6) Comment: The Georgia
Department of Transportation (GDOT)
commented that an occurrence located
in a transportation right-of-way in
Chattooga County, Georgia, is on lands
owned by GDOT. GDOT also
commented on its collaborative efforts
with Georgia Power and ABG to manage
the habitat and white fringeless orchid
population at this site.
Our Response: We include this
information in this rule by adding
GDOT to Table 2, above, which reports
the number of occurrences on publicly
owned or managed lands, and by
discussing conservation efforts to
restore this population under the
heading Summary of Biological Status
and Threats, below.
Lhorne on DSK30JT082PROD with RULES
Public Comments
(7) Comment: We received one
comment recommending against listing
the white fringeless orchid as threatened
or endangered. The commenter stated
that this opinion was based on the
following: (1) The funds and human
hours that would be spent on the white
fringeless orchid could be spent
elsewhere, such as on priority species;
and (2) the species has already declined
in great numbers since it became a
candidate for listing in 1999, and it
seems like more information is needed
to allow for preparation of a recovery
plan for the species.
Our Response: The Act (16 U.S.C.
1531 et seq.) requires the Service to
identify species of wildlife and plants
that are endangered or threatened, based
on the best available scientific and
commercial data. As discussed in the
proposed rule (80 FR 55304; September
15, 2015) and as summarized here, we
have determined the threats to the white
fringeless orchid warrant its listing as
threatened under the Act.
Regarding the commenter’s assertion
that the species has already declined in
great numbers since 1999, the Service
acknowledges that some populations
have been lost or have declined since
the species became a candidate for
listing, but notes that several new
populations have been discovered since
that time. The Service’s determination
to list the species as threatened, rather
than endangered, reflects our
conclusion that the species is not at
imminent risk of extinction. Further,
contrary to the commenter’s assertion
that more information is needed to
prepare a recovery plan, there are
considerable biological data available,
as summarized in the proposed rule (80
FR 55304; September 15, 2015), upon
which a recovery plan can be based, as
VerDate Sep<11>2014
15:24 Sep 12, 2016
Jkt 238001
well as ongoing conservation efforts that
the Service and its partners can build
upon and learn from as we develop a
recovery plan for the white fringeless
orchid.
(8) Comment: We received comments
from four individuals or organizations
recommending that we designate critical
habitat for white fringeless orchid. Two
of the commenters provided no
information or data to support their
recommendations. One commenter
suggested that critical habitat would
benefit conservation efforts for the white
fringeless orchid for the following
reasons: Most of the threats described in
the proposed listing rule are related to
habitat disturbance or loss; many
populations are small and, in the
commenter’s opinion, would likely no
longer exist absent critical habitat
designation; and the threat of
unauthorized collection is, in the
commenter’s opinion, neither imminent
nor present. This commenter also
suggested that a threatened species
would experience protective benefits
from critical habitat designation because
of the requirement for Federal agencies
to consult with the Service about
projects that could potentially adversely
affect critical habitat. Another
commenter who recommended
designating critical habitat cited the
habitat specificity of the species and
threats from human activity, such as
logging and construction, as the reasons
for this recommendation.
Our Response: In the proposed rule
(80 FR 55304; September 15, 2015), we
weighed the expected increase in threats
associated with a critical habitat
designation against the benefits that
might be gained by a critical habitat
designation. We acknowledge that, as
two commenters observed, most of the
threats described in the proposed rule
are related to disturbance or destruction
of habitat. However, many of the threats
to habitat would not be alleviated by
designation of critical habitat, as they
are not caused by actions or
undertakings of Federal agencies.
Section 7(a)(2) of the Act requires
Federal agencies, including the Service,
to ensure that actions they fund,
authorize, or carry out are not likely to
jeopardize the continued existence of
any endangered or threatened species or
result in the destruction or adverse
modification of that species’ critical
habitat. Critical habitat only provides
protections where there is a Federal
nexus, that is, those actions that come
under the purview of section 7 of the
Act. Critical habitat designation has no
application to actions that do not have
a Federal nexus, including logging and
construction on privately owned lands.
PO 00000
Frm 00021
Fmt 4700
Sfmt 4700
62829
Section 7(a)(2) of the Act mandates that
Federal agencies, in consultation with
the Service, evaluate the effects of its
proposed action on any designated
critical habitat. Similar to the Act’s
requirement that a Federal agency
action not jeopardize the continued
existence of listed species, Federal
agencies have the responsibility not to
implement actions that would destroy
or adversely modify designated critical
habitat. Critical habitat designation
alone, however, does not require that a
Federal action agency implement
specific steps toward species recovery.
Some of the populations on Federal
lands are the largest known, and any
future activity involving a Federal
action that would destroy or adversely
modify critical habitat at these sites
would also likely jeopardize the species’
continued existence. Consultation with
respect to critical habitat would provide
additional protection to a species only
if the agency action would result in the
destruction or adverse modification of
the critical habitat but would not
jeopardize the continued existence of
the species. In the absence of a critical
habitat designation, areas that support
white fringeless orchid will continue to
be subject to conservation actions
implemented under section 7(a)(1) of
the Act and to the regulatory protections
afforded by the section 7(a)(2) jeopardy
standard, as appropriate.
We disagree with one commenter’s
assertion that because most populations
are small they likely would no longer
exist absent a critical habitat
designation. On the contrary, the fact
that most of the populations are small,
combined with the fact that they are
located in remote sites that are
infrequently monitored by conservation
organizations or law enforcement, led
the Service to conclude that publishing
locations of those populations in maps
that would be required for a critical
habitat designation would heighten the
threat of collection. In small
populations, the collection of even a few
individuals would diminish
reproductive output and likely reduce
genetic diversity, reducing the resilience
of those populations to recover from
other threats to habitat or individual
plants.
Despite one commenter’s assertion
that the threat of collection is neither
imminent nor present, the proposed rule
documented that this threat is both
present and imminent, as observed by
Service and Tennessee Department of
Environment and Conservation (TDEC)
biologists during 2014. Identification of
critical habitat would increase the
magnitude and severity of this threat by
spatially depicting exactly where the
E:\FR\FM\13SER1.SGM
13SER1
62830
Federal Register / Vol. 81, No. 177 / Tuesday, September 13, 2016 / Rules and Regulations
species may be found and widely
publicizing this information, exposing
these fragile populations and their
habitat to greater risks. We have
reviewed management plans and other
documents produced by Federal and
State conservation agencies and
scientific literature, and detailed
information on the specific locations of
white fringeless orchid sites is not
currently available.
(9) Comment: We received comments
from Georgia Power informing us of
conservation efforts directed towards a
roadside population in Chattooga
County, Georgia, which also lies within
a power transmission right-of-way.
Georgia Power also commented on its
collaborative efforts with GDNR to
monitor, protect, and manage the
occurrence located on GDNR lands in
Rabun County, Georgia.
Our Response: We have included this
information under the heading
Summary of Biological Status and
Threats.
Lhorne on DSK30JT082PROD with RULES
Summary of Changes From the
Proposed Rule
Based on these comments, in this
final rule, we include two minor
changes from the proposed listing rule
(80 FR 55304; September 15, 2015).
Those changes are discussed above
under the heading Distribution.
Additionally, under the heading
Summary of Biological Status and
Threats, we include a discussion of
conservation efforts based on comments
we received from GDOT and Georgia
Power.
Summary of Biological Status and
Threats
Section 4 of the Act (16 U.S.C. 1533),
and its implementing regulations at 50
CFR part 424, set forth the procedures
for adding species to the Federal Lists
of Endangered and Threatened Wildlife
and Plants. Under section 4(a)(1) of the
Act, we may list a species based on 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; and (E)
other natural or manmade factors
affecting its continued existence. Listing
may be warranted based on any of the
above threat factors, singly or in
combination. Each of these factors is
discussed below.
In the proposed listing rule (80 FR
55304; September 15, 2015), we
carefully assessed the best scientific and
commercial information available
VerDate Sep<11>2014
15:24 Sep 12, 2016
Jkt 238001
regarding the past, present, and future
threats to the white fringeless orchid
and provided a detailed account of
those threats and the biological status of
white fringeless orchid.
We have determined that the threats
to white fringeless orchid consist
primarily of destruction and
modification of habitat (Factor A)
resulting in excessive shading, soil
disturbance, altered hydrology, and
proliferation of invasive plant species;
collecting for recreational or commercial
purposes (Factor B); herbivory (Factor
C); and small population sizes and
dependence on specific pollinators and
fungi to complete its life cycle (Factor
E). Existing regulatory mechanisms have
not led to a reduction or removal of
threats posed to the species from these
factors (Factor D). We summarize each
of those threats here. Please refer to the
proposed listing rule (80 FR 55304;
September 15, 2015) for the full
discussion.
Habitat destruction and modification
(Factor A) from development,
silvicultural practices, excessive
shading, and altered hydrology (i.e.,
pond construction, beaver dam removal)
have resulted in extirpation of the
species from 10 sites (Shea 1992, pp. 15,
25; TDEC 2014). These threats, in
addition to invasive plant species (U.S.
Forest Service (USFS) 2008, p. 53;
Richards 2013, pers. comm.; KSNPC
2014; TDEC 2014), feral hogs (Zettler
1994, p. 687; USFS 2008, p. 54;
Richards 2013, pers. comm.; Richards
2014, pers. comm.; Tackett 2015, pers.
comm.), and right-of-way maintenance
(Taylor 2014, pers. comm.), are
associated with habitat modifications
affecting dozens of other occurrences
that are extant or of uncertain status.
The best available information indicates
that habitat for many existing
populations is adversely affected by
factors that either directly harm
individual white fringeless orchids or
alter the plant communities, soils, and
water flow in the sites where they occur.
These factors include residential
development, utility and road right-ofway maintenance, timber harvesting,
invasive species encroachment, and
vegetation succession in the absence of
disturbance. Impacts to habitat from
activities such as development and
silvicultural practices include direct
impacts such as habitat conversion and
ground disturbance, and indirect
impacts such as altered hydrology,
increased shading, and introduction of
invasive, nonnative plants. The threats
to the white fringeless orchid from
habitat destruction and modification are
occurring throughout much of the
species’ range and these population-
PO 00000
Frm 00022
Fmt 4700
Sfmt 4700
level impacts are expected to continue
into the foreseeable future.
During the comment period, GDOT
and Georgia Power provided
information on conservation efforts that
have been directed to a roadside
occurrence in Chattooga County,
Georgia, which is located in a power
transmission right-of-way. As noted in
the proposed listing rule (80 FR 55304;
September 15, 2015), this site was
adversely affected by unauthorized
collection in 2004, and remains
vulnerable to this threat due to its
location alongside a State highway.
Georgia Power and GDOT have
designated this site an
‘‘Environmentally Sensitive Area,’’
restricting mowing and herbicide use.
They are also working with ABG to
augment the population at this
occurrence with plants propagated from
seed collected at this site. Georgia
Power is also collaborating with GDNR
to protect, monitor, and manage another
occurrence, located in Rabun County,
Georgia, and reported that a prescribed
burn was recently conducted in the area
where this occurrence is located. ABG
staff have collected seeds from this
population to produce propagated
plants that will be used to augment the
population at this occurrence.
Collecting for scientific, recreational,
or commercial purposes (Factor B) has
been determined to be the cause for
extirpation of the white fringeless
orchid at its type locality (Ettman and
McAdoo 1979 cited in Zettler and
Fairey 1990, p. 212), and recent
evidence demonstrates that collection
remains a threat to this species. Fungal
pathogens have been identified as a
threat to white fringeless orchid, but a
threat with potentially greater impact
associated with Factor C is inflorescence
herbivory, presumably by deer (Zettler
and Fairey 1990, p. 212–214). Flower
herbivory has been reported at over onethird of extant occurrences and likely is
a factor threatening most white
fringeless orchid occurrences (Shea
1992, pp. 27, 61, 71–77, 95–97; TDEC
2012, p. 3; KSNPC 2014; TDEC 2014),
especially where low numbers of plants
are present. Tuber herbivory or soil
disturbance by feral hogs has been
reported at multiple occurrences,
including the site harboring the largest
known white fringeless orchid
population (Zettler 1994, p. 687; USFS
2008, p. 54).
The effects of all of the abovedescribed threats are intensified by the
small population sizes that characterize
a majority of occurrences throughout the
species’ geographic range (Factor E), due
to their diminished capacity to recover
from loss of individuals or low
E:\FR\FM\13SER1.SGM
13SER1
Federal Register / Vol. 81, No. 177 / Tuesday, September 13, 2016 / Rules and Regulations
Lhorne on DSK30JT082PROD with RULES
reproductive output resulting from other
threats (Zettler et al. 1996, p. 22).
Further, the species’ dependence on a
limited number of Lepidoptera (Zettler
et al. 1996, p. 16) and a single species
of fungi (Currah et al. 1997, p. 30) to
complete its life cycle make it
vulnerable to disturbances that diminish
habitat suitability for these taxa as well
(Factor E). Climate has changed in
recent decades in the southeastern
United States, and the rate of change
likely will continue to increase into the
future (Karl et al. 2009, pp. 111–112)
(Factor E). Although we do not have
data to determine specifically how the
habitats where the white fringeless
orchid occurs will be affected by, or
how the species will respond to, these
changes, the potential for adverse effects
to the white fringeless orchid, either
through changes in habitat suitability or
effects on populations of pollinators or
mycorrhizal fungi, is likely to increase
as climate continues to change at an
accelerating rate.
Determination
Section 4 of the Act (16 U.S.C. 1533),
and its implementing regulations at 50
CFR part 424, set forth the procedures
for adding species to the Federal Lists
of Endangered and Threatened Wildlife
and Plants. 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 white fringeless orchid is
likely to become endangered throughout
all or a significant portion of its range
within the foreseeable future based on
the low to moderate threats currently
impacting the species. The species is
known to be extant at 57 locations (see
Table 1, above), but low numbers of
individuals have been observed at more
than half of these (see Figure 1 in the
proposed listing rule: 80 FR 55304,
September 15, 2015, p. 55309),
distributed across the species’ range,
and their persistence into the future is
uncertain. Furthermore, the threats of
habitat destruction or modification and
herbivory are present throughout the
species’ geographic range. Left
unmanaged, these threats will likely
lead to further reductions in the species’
geographic range and abundance at
individual sites, increasing the risk of
extinction to the point of endangerment.
The combination of small population
sizes combined with the white
fringeless orchid’s dependence on
specific pollinators and fungi to
complete its life cycle diminishes the
VerDate Sep<11>2014
15:24 Sep 12, 2016
Jkt 238001
resilience of populations to recover from
adverse effects of threats due to habitat
destruction or modification and
herbivory.
Therefore, on the basis of the best
available scientific and commercial
information, we are listing the white
fringeless orchid as threatened in
accordance with sections 3(20) and
4(a)(1) of the Act. The species does not
currently meet the definition of
endangered species, because a sufficient
number of robust populations are
present on publicly owned or managed
lands, which despite numerous threats,
are actively managed such that the risk
of extinction is not imminent.
Furthermore, conservation efforts have
been initiated that could be effective in
reducing threats by increasing
population sizes and improving habitat
conditions across much of the species’
geographic 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 white fringeless orchid 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).
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 requires
that recovery actions be carried out for
all 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 requires the Service to develop
and implement recovery plans for the
conservation of endangered and
PO 00000
Frm 00023
Fmt 4700
Sfmt 4700
62831
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, selfsustaining, 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. The recovery plan identifies sitespecific management actions that set a
trigger for review of the five factors that
control whether a species remains
endangered or may be downlisted or
delisted, 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. Revisions
of the plan may be done to address
continuing or new threats to the species,
as new substantive information becomes
available. Recovery teams (composed of
species experts, Federal and State
agencies, nongovernmental
organizations, and stakeholders) are
often established to develop recovery
plans. When completed, the recovery
outline, draft recovery plan, and the
final recovery plan will be available on
our Web site (https://www.fws.gov/
endangered) or from our Tennessee
Ecological Services Field Office (see FOR
FURTHER INFORMATION CONTACT).
Implementation of recovery actions
generally requires the participation of a
broad range of partners, including other
Federal agencies, States, Tribes,
nongovernmental organizations,
businesses, and private landowners.
Examples of recovery actions include
habitat restoration (e.g., restoration of
native vegetation), research, captive
propagation and reintroduction, and
outreach and education. The recovery of
many listed species cannot be
accomplished solely on Federal lands
because their 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.
Following publication of this final
listing rule, 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
E:\FR\FM\13SER1.SGM
13SER1
Lhorne on DSK30JT082PROD with RULES
62832
Federal Register / Vol. 81, No. 177 / Tuesday, September 13, 2016 / Rules and Regulations
organizations. In addition, pursuant to
section 6 of the Act, the States of
Georgia, South Carolina, Alabama,
Mississippi, and Tennessee and the
Commonwealth of Kentucky will be
eligible for Federal funds to implement
management actions that promote the
protection or recovery of the white
fringeless orchid. Information on our
grant programs that are available to aid
species recovery can be found at: https://
www.fws.gov/grants.
Please let us know if you are
interested in participating in recovery
efforts for the white fringeless orchid.
Additionally, we invite you to submit
any new information on this species
whenever it becomes available and any
information you may have for recovery
planning purposes (see FOR FURTHER
INFORMATION CONTACT).
Section 7(a) of the Act requires
Federal agencies to evaluate their
actions with respect to any species that
is 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)(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 any endangered or
threatened 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
consultation, as described in the
preceding paragraph, include
management and any other landscapealtering activities on Federal lands
administered by the U.S. Fish and
Wildlife Service, U.S. Forest Service
(USFS), and National Park Service
(NPS); issuance of section 404 Clean
Water Act (33 U.S.C. 1251 et seq.)
permits by the U.S. Army Corps of
Engineers; powerline right-of-way
construction and maintenance by the
TVA; and construction and maintenance
of roads or highways by the Federal
Highway Administration.
The Act and its implementing
regulations set forth a series of general
prohibitions and exceptions that apply
to endangered and threatened plants.
With regard to threatened plants, 50
CFR 17.71 provides that all of the
prohibitions in 50 CFR 17.61 applicable
to endangered plants apply to
threatened plants, with one exception.
Thus, the regulations at 50 CFR 17.71(a)
make it illegal for any person subject to
VerDate Sep<11>2014
15:24 Sep 12, 2016
Jkt 238001
the jurisdiction of the United States to
import or export, transport in interstate
or foreign commerce in the course of a
commercial activity, sell or offer for sale
in interstate or foreign commerce, or
remove and reduce the species to
possession from areas under Federal
jurisdiction any threatened plant. There
is an exception for the seeds of
cultivated specimens, provided that a
statement that the seeds are of
‘‘cultivated origin’’ accompanies the
seeds or their container. The Act itself,
at 16 U.S.C. 1538(a)(2)(B), prohibits
malicious damage or destruction of any
such species on any area under Federal
jurisdiction, and the removal, cutting,
digging up, or damaging or destroying of
any such species on any other area in
knowing violation of any State law or
regulation, or in the course of any
violation of a State criminal trespass
law.
Under 50 CFR 17.72, we may issue
permits to carry out otherwise
prohibited activities involving
threatened plants under certain
circumstances. A permit issued under
this section must be for one of the
following: Scientific purposes, the
enhancement of the propagation or
survival of threatened species, economic
hardship, botanical or horticultural
exhibition, educational purposes, or
other activities consistent with the
purposes and policy 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 final listing on proposed
and ongoing activities within the range
of a listed species. 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:
(1) Unauthorized collecting, handling,
possessing, selling, delivering, carrying,
or transporting of white fringeless
orchid, including interstate
transportation across State lines and
import or export across international
boundaries, except for properly
documented antique specimens of this
species at least 100 years old, as defined
by section 10(h)(1) of the Act;
(2) Unauthorized removal, damage, or
destruction of white fringeless orchid
plants from populations located on
Federal land (USFS, NPS, and Service
lands); and
(3) Unauthorized removal, damage, or
destruction of white fringeless orchid
plants on private land in violation of
PO 00000
Frm 00024
Fmt 4700
Sfmt 4700
any State regulation, including criminal
trespass.
At this time, we are unable to identify
specific activities that would not be
considered to result in a violation of
section 9 of the Act because the white
fringeless orchid occurs in a variety of
habitat conditions across its range and
it is likely that site-specific conservation
measures may be needed for activities
that may directly or indirectly affect the
species. Questions regarding whether
specific activities would constitute a
violation of section 9 of the Act should
be directed to the Tennessee Ecological
Services Field Office (see FOR FURTHER
INFORMATION CONTACT).
Required Determinations
National Environmental Policy Act (42
U.S.C. 4321 et seq.)
We have determined that
environmental assessments and
environmental impact statements, as
defined under the authority of the
National Environmental Policy Act,
need not be prepared in connection
with listing a species as an endangered
or threatened species under the
Endangered Species Act. We published
a notice outlining our reasons for this
determination in the Federal Register
on October 25, 1983 (48 FR 49244).
References Cited
A complete list of references cited in
this rulemaking is available on the
Internet at https://www.regulations.gov
and upon request from the Tennessee
Ecological Services Field Office (see FOR
FURTHER INFORMATION CONTACT).
Authors
The primary authors of this final rule
are the staff members of the Tennessee
Ecological Services Field Office.
List of Subjects in 50 CFR Part 17
Endangered and threatened species,
Exports, Imports, Reporting and
recordkeeping requirements,
Transportation.
Regulation Promulgation
Accordingly, we amend part 17,
subchapter B of chapter I, title 50 of the
Code of Federal Regulations, as follows:
PART 17—ENDANGERED AND
THREATENED WILDLIFE AND PLANTS
1. The authority citation for part 17
continues to read as follows:
■
Authority: 16 U.S.C. 1361–1407; 1531–
1544; and 4201–4245, unless otherwise
noted.
2. Amend § 17.12(h) by adding an
entry for ‘‘Platanthera integrilabia’’ to
the List of Endangered and Threatened
■
E:\FR\FM\13SER1.SGM
13SER1
62833
Federal Register / Vol. 81, No. 177 / Tuesday, September 13, 2016 / Rules and Regulations
§ 17.12
Plants in alphabetical order under
FLOWERING PLANTS to read as
follows:
Scientific name
*
Endangered and threatened plants.
*
*
(h) * * *
*
*
Common name
Where listed
*
*
White fringeless orchid ...
Status
*
Wherever found ..............
Listing citations and applicable rules
FLOWERING PLANTS
*
Platanthera integrilabia ...
*
*
*
Dated: August 23, 2016.
James W. Kurth,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2016–21954 Filed 9–12–16; 8:45 am]
BILLING CODE 4333–15–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 679
[Docket No. 150916863–6211–02]
RIN 0648–XE867
Fisheries of the Exclusive Economic
Zone Off Alaska; Exchange of Flatfish
in the Bering Sea and Aleutian Islands
Management Area
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Temporary rule; reallocation.
AGENCY:
NMFS is exchanging unused
rock sole Community Development
Quota (CDQ) for yellowfin sole CDQ
SUMMARY:
*
T
*
*
*
81 FR [Insert Federal Register page where the
document begins]; September 13, 2016.
*
acceptable biological catch (ABC)
reserves in the Bering Sea and Aleutian
Islands management area. This action is
necessary to allow the 2016 total
allowable catch of yellowfin sole in the
Bering Sea and Aleutian Islands
management area to be harvested.
DATES: Effective September 13, 2016
through December 31, 2016.
FOR FURTHER INFORMATION CONTACT:
Steve Whitney, 907–586–7228.
SUPPLEMENTARY INFORMATION: NMFS
manages the groundfish fishery in the
Bering Sea and Aleutian Islands
management area (BSAI) according to
the Fishery Management Plan for
Groundfish of the Bering Sea and
Aleutian Islands Management Area
(FMP) prepared by the North Pacific
Fishery Management Council under
authority of the Magnuson-Stevens
Fishery Conservation and Management
Act. Regulations governing fishing by
U.S. vessels in accordance with the FMP
appear at subpart H of 50 CFR part 600
and 50 CFR part 679.
The 2016 rock sole and yellowfin sole
CDQ reserves specified in the BSAI are
6,160 metric tons (mt), and 15,773 mt as
established by the final 2016 and 2017
*
*
harvest specifications for groundfish in
the BSAI (81 FR 14773, March 18, 2016)
and following revision (81 FR 48722,
July 26, 2016). The 2016 rock sole and
yellowfin sole CDQ ABC reserves are
11,078 mt and 6,879 mt as established
by the final 2016 and 2017 harvest
specifications for groundfish in the
BSAI (81 FR 14773, March 18, 2016)
and following revision (81 FR 48722,
July 26, 2016).
The Aleutian Pribilof Island
Community Development Association
has requested that NMFS exchange 700
mt of rock sole CDQ reserves for 700 mt
of yellowfin sole CDQ ABC reserves
under § 679.31(d). Therefore, in
accordance with § 679.31(d), NMFS
exchanges 700 mt of rock sole CDQ
reserves for 700 mt of yellowfin sole
CDQ ABC reserves in the BSAI. This
action also decreases and increases the
TACs and CDQ ABC reserves by the
corresponding amounts. Tables 11 and
13 of the final 2016 and 2017 harvest
specifications for groundfish in the
BSAI (81 FR 14773, March 18, 2016),
and following revision (81 FR 48722,
July 26, 2016), are revised as follows:
TABLE 11—FINAL 2016 COMMUNITY DEVELOPMENT QUOTA (CDQ) RESERVES, INCIDENTAL CATCH AMOUNTS (ICAS), AND
AMENDMENT 80 ALLOCATIONS OF THE ALEUTIAN ISLANDS PACIFIC OCEAN PERCH, AND BSAI FLATHEAD SOLE, ROCK
SOLE, AND YELLOWFIN SOLE TACS
[Amounts are in metric tons]
Pacific ocean perch
Lhorne on DSK30JT082PROD with RULES
Sector
Eastern
Aleutian
District
TAC ..........................................................
CDQ .........................................................
ICA ...........................................................
BSAI trawl limited access ........................
Amendment 80 .........................................
Alaska Groundfish Cooperative ...............
Alaska Seafood Cooperative ...................
7,900
845
200
685
6,169
3,271
2,898
Central
Aleutian
District
Flathead sole
Western
Aleutian
District
7,000
749
75
618
5,558
2,947
2,611
9,000
963
10
161
7,866
4,171
3,695
Rock sole
Yellowfin sole
BSAI
BSAI
BSAI
20,585
1,832
5,000
0
13,753
1,411
12,342
Note: Sector apportionments may not total precisely due to rounding.
VerDate Sep<11>2014
15:24 Sep 12, 2016
Jkt 238001
PO 00000
Frm 00025
Fmt 4700
Sfmt 4700
E:\FR\FM\13SER1.SGM
13SER1
56,450
5,460
6,000
0
44,990
11,129
33,861
145,065
16,473
3,500
14,979
110,113
43,748
66,365
Agencies
[Federal Register Volume 81, Number 177 (Tuesday, September 13, 2016)]
[Rules and Regulations]
[Pages 62826-62833]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2016-21954]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS-R4-ES-2015-0129; 4500030113]
RIN 1018-BA93
Endangered and Threatened Wildlife and Plants; Threatened Species
Status for Platanthera integrilabia (White Fringeless Orchid)
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), determine
threatened species status under the Endangered Species Act of 1973
(Act), as amended, for Platanthera integrilabia (white fringeless
orchid), a plant species from Alabama, Georgia, Kentucky, Mississippi,
South Carolina, and Tennessee. This rule adds this species to the
Federal List of Endangered and Threatened Plants.
DATES: This rule is effective October 13, 2016.
ADDRESSES: This final rule is available on the Internet at https://www.regulations.gov and https://www.fws.gov/cookeville. Comments and
materials we received, as well as supporting documentation we used in
preparing this rule, are available for public inspection at https://www.regulations.gov, or by appointment, during normal business hours,
at: U.S. Fish and Wildlife Service, Tennessee Ecological Services Field
Office, 446 Neal Street, Cookeville, TN 38501; telephone: 931-528-6481;
facsimile: 931-528-7075.
FOR FURTHER INFORMATION CONTACT: Mary Jennings, Field Supervisor, U.S.
Fish and Wildlife Service, Tennessee Ecological Services Field Office
(see ADDRESSES, above). Persons who use a telecommunications device for
the deaf (TDD) may call the Federal Information Relay Service (FIRS) at
800-877-8339.
SUPPLEMENTARY INFORMATION:
Previous Federal Actions
Please refer to the proposed listing rule for the white fringeless
orchid (80 FR 55304; September 15, 2015) for a detailed description of
previous Federal actions concerning this species.
Background
Below, we update and summarize information from the proposed
listing rule for the white fringeless orchid (80 FR 55304; September
15, 2015) on the historical and current distribution of white
fringeless orchid. Please refer to the proposed listing rule for a
summary of other species information, including habitat, biology, and
genetics.
Distribution
In this final rule, we are updating information on the species'
distribution from the September 15, 2015, proposed rule to include two
minor changes, which were brought to our attention following
publication of the proposed listing rule. First, we are changing the
2014 status of the Forsyth County, Georgia, population from extant to
uncertain (Table 1), because flowering plants have not been documented
at this site since 1990 (Richards 2015, pers. comm.). In addition, we
have added Georgia Department of Transportation (GDOT) to the list of
local, State, or Federal government entities that own or manage lands
where white fringeless orchid is present (Table 2). A revised summary
of the species' distribution follows.
Table 1--County-Level Distribution of Extant and Uncertain Status White Fringeless Orchid Occurrences, Circa
1991 (Shea 1992) and 2014 (ANHP 2014, GDNR 2014, KSNPC 2014, MDWFP 2014, NCDENR 2014, SCDNR 2012, Schotz 2015,
and TDEC 2014)
----------------------------------------------------------------------------------------------------------------
1991 2014
State County ---------------------------------------------------------------
Extant Uncertain Extant Uncertain
----------------------------------------------------------------------------------------------------------------
Alabama....................... Calhoun......... .............. .............. 2 ..............
Clay............ .............. 1 1 ..............
Cleburne........ .............. .............. 1 ..............
DeKalb.......... .............. .............. 1 ..............
Jackson......... .............. .............. .............. 1
Marion.......... 1 .............. 1 2
Tuscaloosa...... 1 .............. 1 ..............
Winston......... 1 .............. 1 ..............
Georgia....................... Bartow.......... .............. .............. 1 ..............
Carroll......... 2 .............. 2 ..............
Chattooga....... .............. .............. 1 ..............
Cobb............ 1 .............. .............. ..............
Coweta.......... 1 .............. 1 ..............
Forsyth......... .............. 1 .............. 1
Pickens......... .............. .............. 1 ..............
Rabun........... 1 .............. 1 ..............
Stephens........ 1 .............. 1 ..............
Kentucky...................... Laurel.......... .............. .............. 2 2
McCreary........ 4 .............. 2 1
Pulaski......... 1 1 2 ..............
Whitley......... .............. .............. 1 ..............
Mississippi................... Alcorn.......... .............. .............. .............. 1
Itawamba........ .............. .............. 2 1
Tishomingo...... .............. .............. 1 1
South Carolina................ Greenville...... 1 .............. .............. 1
Tennessee..................... Bledsoe......... .............. 2 2 1
Cumberland...... .............. .............. 1 ..............
Fentress........ .............. .............. 2 ..............
Franklin........ 3 2 5 5
[[Page 62827]]
Grundy.......... 5 5 4 4
Marion.......... 2 .............. 8 ..............
McMinn.......... 1 .............. 1 ..............
Polk............ .............. .............. 1 ..............
Scott........... .............. .............. 1 ..............
Sequatchie...... 2 1 1 1
Van Buren....... 2 .............. 5 1
---------------------------------------------------------------
Total..................... ................ 30 13 57 23
----------------------------------------------------------------------------------------------------------------
Table 2--Status and Number of White Fringeless Orchid Occurrences on Publicly Owned or Managed Lands
[Note: One site is on privately owned lands that the Georgia Department of Natural Resources (GDNR) leases for
use as a wildlife management area]
----------------------------------------------------------------------------------------------------------------
Ownership Extant Uncertain Extirpated Historical
----------------------------------------------------------------------------------------------------------------
National Park Service........................... 3 .............. .............. ..............
U.S. Forest Service............................. 9 3 3 ..............
U.S. Fish and Wildlife Service.................. 2 .............. .............. ..............
Alabama Department of Conservation and Natural .............. 1 .............. ..............
Resources......................................
Georgia Department of Natural Resources......... 2 .............. .............. ..............
Georgia Department of Transportation............ 1 .............. .............. ..............
Kentucky State Nature Preserves Commission...... 1 .............. .............. 1
Mississippi Department of Fish, Wildlife, and 1 .............. .............. ..............
Parks..........................................
North Carolina Plant Conservation Program....... .............. .............. 1 ..............
South Carolina State Parks...................... .............. 1 .............. ..............
Tennessee Department of Transportation.......... 1 .............. .............. ..............
Tennessee Division of Forestry.................. 7 .............. .............. ..............
Tennessee State Parks........................... 5 1 .............. 1
Tennessee Wildlife Resources Agency............. 1 .............. 1 ..............
Forsyth County, Georgia......................... .............. 1 .............. ..............
---------------------------------------------------------------
Total....................................... 33 7 5 2
----------------------------------------------------------------------------------------------------------------
All other information from the ``Distribution'' discussion in the
proposed rule (80 FR 55304; September 15, 2015) remains unchanged.
Summary of Comments and Recommendations
In the proposed rule published on September 15, 2015 (80 FR 55304),
we requested that all interested parties submit written comments on the
proposal by November 16, 2015. We also contacted appropriate Federal
and State agencies, scientific experts and organizations, and other
interested parties and invited them to comment on the proposal. On
April 14, 2016 (81 FR 22041), we reopened the comment period for an
additional 60 days, ending June 13, 2016. Newspaper notices inviting
general public comment were published in the Asheville Citizen Times,
Birmingham News, Chattanooga Times Free Press, Greenville News,
Huntsville News, Knoxville News, Lexington Herald-Leader, and Northeast
Mississippi Daily Journal. We did not receive any requests for a public
hearing.
Peer Reviewer Comments
In accordance with our peer review policy published on July 1, 1994
(59 FR 34270), we solicited expert opinion from three knowledgeable
individuals with scientific expertise that included familiarity with
white fringeless orchid and its habitat, biological needs, and threats
or general conservation biology of orchids. We received responses from
two of the peer reviewers. We reviewed all comments we received from
the peer reviewers for substantive issues and new information regarding
the listing of white fringeless orchid. The peer reviewers generally
concurred with our evaluation and the conclusion we reached regarding
the proposal to list the white fringeless orchid as a threatened
species. One peer reviewer commented on the information on the species'
habitat, biology, and threats, and provided minor updates regarding the
status and distribution of white fringeless orchid in the State of
Georgia. Peer reviewer comments are addressed in the following summary
and incorporated into the final rule as appropriate.
(1) Comment: One reviewer commented on subtle differences in
descriptions of white fringeless orchid habitat that have been recorded
over time, suggesting that descriptions from the 1970s (Luer 1975, p.
186; Shea 1992, p. 19) or later might represent altered conditions, as
compared to the earliest published habitat description (Correll 1941,
pp. 156-157). This reviewer noted that Correll (1941, pp. 156-157) used
the term ``grassy,'' citing an herbarium specimen label, in describing
the habitat, possibly implying the presence of more open conditions in
which a grassy herbaceous community would have been present. This
reviewer speculated that the shaded, forested conditions, discussed in
more contemporary descriptions of white fringeless orchid habitat,
might have
[[Page 62828]]
resulted from land use and regulatory changes (i.e., regulation of
impacts to wetlands) that have favored the development of more densely
stocked, heavily shaded contemporary forest conditions in habitats
where the white fringeless orchid occurs. This reviewer opined that
current habitat conditions where the white fringeless orchid occurs do
not, in many cases, represent the optimal range of habitat variation
for the species. This reviewer also cited short-term positive responses
of white fringeless orchid populations to timber removal in adjacent
uplands, a phenomenon that we discussed in the proposed listing rule,
as evidence of the positive influences of increased light and water
availability, but which diminish with regrowth of even-aged hardwood
stands in the absence of ecological disturbance, such as fire. One
commenter also suggested that fire could be a beneficial management
tool in conservation efforts for the white fringeless orchid.
Our Response: We agree with the peer reviewer's observations about
the potential beneficial effects of ecological disturbance, such as
fire, in creating environmental conditions that stimulate population
growth and increased flower production in the white fringeless orchid.
The proposed listing rule (80 FR 55304; September 15, 2015) discusses
short-term positive responses to timber harvesting that have been
observed in some white fringeless orchid populations and notes that
Schotz (2015, p. 4) suggested that fire could play a role in regulating
woody vegetation growth in uplands surrounding white fringeless orchid
habitats. The proposed rule also reports on Hoy's (2012, p. 26)
suggestion that high stem densities, which resulted from succession
following canopy removal, shortened the hydroperiod of wetlands at a
white fringeless orchid site in Kentucky. Evaluating the potential role
of fire or other ecological disturbance in managing habitat for the
white fringeless orchid will be considered during preparation of a
recovery plan (see discussion about recovery plans under the heading
Available Conservation Measures, below) for the species after it is
listed.
(2) Comment: One peer reviewer commented that the use of herbicides
on industrial and small-scale timber operations appears to be
increasing significantly in the State of Georgia and that we should
include it as a threat of significant concern not only to the white
fringeless orchid but also to the herbaceous plant community of which
it is part, as well as pollinators. The reviewer did not provide
specific data in support of this comment.
Our Response: We agree that increased use of herbicides in timber
operations in or near habitats where the white fringeless orchid occurs
could be detrimental to the species, as well as other herbaceous plants
and pollinators, but we are not aware of specific instances where
adverse effects to the white fringeless orchid have occurred due to
herbicide use in silvicultural operations, nor do we have data
regarding the rates at which herbicides are used in silvicultural
operations presently or in the past. Therefore, we have not added a
discussion of herbicide use in silvicultural operations in the analysis
of factors affecting the white fringeless orchid.
(3) Comment: One peer reviewer commented that Atlanta Botanical
Garden (ABG) has developed asymbiotic (in the absence of symbiotic
fungi), aseptic (free from contamination caused by harmful bacteria,
viruses, or other microorganisms) in vitro propagation protocols that
achieve much higher germination rates than the rate (less than 3
percent) observed by other researchers in separate studies of in vitro
and in situ seedling development (Zettler and McInnis 1992, pp. 157-
160; Zettler 1994, p. 65).
Our Response: The Service is aware of the success that ABG has
achieved in propagating the white fringeless orchid; however, we are
not aware of specific rates of seedling germination that we can include
in this rule. Effective propagation protocols could be a valuable tool,
combined with science-based habitat management practices, for
augmenting currently small populations or restoring populations in
sites where the species is no longer extant but suitable habitat
conditions remain. We will consider this information during development
of a recovery plan for the species.
(4) Comment: One peer reviewer commented on the discussion in the
proposed listing rule about rates of fruit set in relation to
population size, which cited Zettler et al. (1996, p. 22) and Zettler
and McInnis (1992, p. 160) in suggesting that inbreeding depression
could be a cause for the lower fruit set observed in smaller
populations. The peer reviewer commented that low census numbers of
flowering individuals and highly fragmented or degraded pollinator
networks also could influence the low rates observed in smaller
populations.
Our Response: We agree with the peer reviewer that other factors
besides inbreeding depression, caused by increased rates of self-
pollination, could contribute to low rates of fruit set in small
populations of the white fringeless orchid. However, we are not aware
of specific data that indicate what those other factors might be.
Federal Agency Comments
(5) Comment: The Tennessee Valley Authority (TVA) commented that
nearly 20 percent of extant white fringeless orchid occurrences are
located in transportation or utility rights-of-way, illustrating that
the species occurs in these settings at a disproportionately high rate
when compared to their overall prevalence on the landscape. The TVA
also commented that the proposed rule highlights the beneficial role
that vegetation maintenance, if properly conducted, can play in
maintaining suitable habitat for the white fringeless orchid and that
herbicide resistance in the species could, in part, explain the
positive response seen in one population following herbicide
application in a TVA right-of-way.
Our Response: We acknowledge that current distribution data
indicate that the white fringeless orchid occurs in transportation or
utility rights-of-way at a disproportionately high rate compared to the
overall prevalence of these features on the landscape. One possible
cause for the disproportionally high numbers of populations known from
rights-of-way is that these areas are surveyed by TVA and other utility
or transportation departments more frequently or intensively than the
forested habitats where most populations are located. It might also be
true that white fringeless orchid populations respond positively to the
well-lit conditions found in rights-of-way, assuming that other threats
related to maintenance or unauthorized use of rights-of-way (e.g., off-
road vehicle use) do not adversely affect the plants or their habitat.
We commend TVA on its efforts to prevent adverse effects to rare
species while conducting vegetation management or infrastructure
maintenance in rights-of-way.
Regarding the comment that herbicide resistance could explain the
species' positive response to selective herbicide application, we are
not aware of any data to support the assertion that the species is
resistant to any registered herbicide products. It is possible that the
selective nature of herbicide application to woody species by TVA or
its contractors, rather than herbicide resistance generally, is
responsible for the positive response seen following one known instance
of potential exposure in a TVA right-of-way. This warrants further
research.
[[Page 62829]]
Comments From States
(6) Comment: The Georgia Department of Transportation (GDOT)
commented that an occurrence located in a transportation right-of-way
in Chattooga County, Georgia, is on lands owned by GDOT. GDOT also
commented on its collaborative efforts with Georgia Power and ABG to
manage the habitat and white fringeless orchid population at this site.
Our Response: We include this information in this rule by adding
GDOT to Table 2, above, which reports the number of occurrences on
publicly owned or managed lands, and by discussing conservation efforts
to restore this population under the heading Summary of Biological
Status and Threats, below.
Public Comments
(7) Comment: We received one comment recommending against listing
the white fringeless orchid as threatened or endangered. The commenter
stated that this opinion was based on the following: (1) The funds and
human hours that would be spent on the white fringeless orchid could be
spent elsewhere, such as on priority species; and (2) the species has
already declined in great numbers since it became a candidate for
listing in 1999, and it seems like more information is needed to allow
for preparation of a recovery plan for the species.
Our Response: The Act (16 U.S.C. 1531 et seq.) requires the Service
to identify species of wildlife and plants that are endangered or
threatened, based on the best available scientific and commercial data.
As discussed in the proposed rule (80 FR 55304; September 15, 2015) and
as summarized here, we have determined the threats to the white
fringeless orchid warrant its listing as threatened under the Act.
Regarding the commenter's assertion that the species has already
declined in great numbers since 1999, the Service acknowledges that
some populations have been lost or have declined since the species
became a candidate for listing, but notes that several new populations
have been discovered since that time. The Service's determination to
list the species as threatened, rather than endangered, reflects our
conclusion that the species is not at imminent risk of extinction.
Further, contrary to the commenter's assertion that more information is
needed to prepare a recovery plan, there are considerable biological
data available, as summarized in the proposed rule (80 FR 55304;
September 15, 2015), upon which a recovery plan can be based, as well
as ongoing conservation efforts that the Service and its partners can
build upon and learn from as we develop a recovery plan for the white
fringeless orchid.
(8) Comment: We received comments from four individuals or
organizations recommending that we designate critical habitat for white
fringeless orchid. Two of the commenters provided no information or
data to support their recommendations. One commenter suggested that
critical habitat would benefit conservation efforts for the white
fringeless orchid for the following reasons: Most of the threats
described in the proposed listing rule are related to habitat
disturbance or loss; many populations are small and, in the commenter's
opinion, would likely no longer exist absent critical habitat
designation; and the threat of unauthorized collection is, in the
commenter's opinion, neither imminent nor present. This commenter also
suggested that a threatened species would experience protective
benefits from critical habitat designation because of the requirement
for Federal agencies to consult with the Service about projects that
could potentially adversely affect critical habitat. Another commenter
who recommended designating critical habitat cited the habitat
specificity of the species and threats from human activity, such as
logging and construction, as the reasons for this recommendation.
Our Response: In the proposed rule (80 FR 55304; September 15,
2015), we weighed the expected increase in threats associated with a
critical habitat designation against the benefits that might be gained
by a critical habitat designation. We acknowledge that, as two
commenters observed, most of the threats described in the proposed rule
are related to disturbance or destruction of habitat. However, many of
the threats to habitat would not be alleviated by designation of
critical habitat, as they are not caused by actions or undertakings of
Federal agencies. Section 7(a)(2) of the Act requires Federal agencies,
including the Service, to ensure that actions they fund, authorize, or
carry out are not likely to jeopardize the continued existence of any
endangered or threatened species or result in the destruction or
adverse modification of that species' critical habitat. Critical
habitat only provides protections where there is a Federal nexus, that
is, those actions that come under the purview of section 7 of the Act.
Critical habitat designation has no application to actions that do not
have a Federal nexus, including logging and construction on privately
owned lands. Section 7(a)(2) of the Act mandates that Federal agencies,
in consultation with the Service, evaluate the effects of its proposed
action on any designated critical habitat. Similar to the Act's
requirement that a Federal agency action not jeopardize the continued
existence of listed species, Federal agencies have the responsibility
not to implement actions that would destroy or adversely modify
designated critical habitat. Critical habitat designation alone,
however, does not require that a Federal action agency implement
specific steps toward species recovery.
Some of the populations on Federal lands are the largest known, and
any future activity involving a Federal action that would destroy or
adversely modify critical habitat at these sites would also likely
jeopardize the species' continued existence. Consultation with respect
to critical habitat would provide additional protection to a species
only if the agency action would result in the destruction or adverse
modification of the critical habitat but would not jeopardize the
continued existence of the species. In the absence of a critical
habitat designation, areas that support white fringeless orchid will
continue to be subject to conservation actions implemented under
section 7(a)(1) of the Act and to the regulatory protections afforded
by the section 7(a)(2) jeopardy standard, as appropriate.
We disagree with one commenter's assertion that because most
populations are small they likely would no longer exist absent a
critical habitat designation. On the contrary, the fact that most of
the populations are small, combined with the fact that they are located
in remote sites that are infrequently monitored by conservation
organizations or law enforcement, led the Service to conclude that
publishing locations of those populations in maps that would be
required for a critical habitat designation would heighten the threat
of collection. In small populations, the collection of even a few
individuals would diminish reproductive output and likely reduce
genetic diversity, reducing the resilience of those populations to
recover from other threats to habitat or individual plants.
Despite one commenter's assertion that the threat of collection is
neither imminent nor present, the proposed rule documented that this
threat is both present and imminent, as observed by Service and
Tennessee Department of Environment and Conservation (TDEC) biologists
during 2014. Identification of critical habitat would increase the
magnitude and severity of this threat by spatially depicting exactly
where the
[[Page 62830]]
species may be found and widely publicizing this information, exposing
these fragile populations and their habitat to greater risks. We have
reviewed management plans and other documents produced by Federal and
State conservation agencies and scientific literature, and detailed
information on the specific locations of white fringeless orchid sites
is not currently available.
(9) Comment: We received comments from Georgia Power informing us
of conservation efforts directed towards a roadside population in
Chattooga County, Georgia, which also lies within a power transmission
right-of-way. Georgia Power also commented on its collaborative efforts
with GDNR to monitor, protect, and manage the occurrence located on
GDNR lands in Rabun County, Georgia.
Our Response: We have included this information under the heading
Summary of Biological Status and Threats.
Summary of Changes From the Proposed Rule
Based on these comments, in this final rule, we include two minor
changes from the proposed listing rule (80 FR 55304; September 15,
2015). Those changes are discussed above under the heading
Distribution. Additionally, under the heading Summary of Biological
Status and Threats, we include a discussion of conservation efforts
based on comments we received from GDOT and Georgia Power.
Summary of Biological Status and Threats
Section 4 of the Act (16 U.S.C. 1533), and its implementing
regulations at 50 CFR part 424, set forth the procedures for adding
species to the Federal Lists of Endangered and Threatened Wildlife and
Plants. Under section 4(a)(1) of the Act, we may list a species based
on 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; and (E) other natural or manmade
factors affecting its continued existence. Listing may be warranted
based on any of the above threat factors, singly or in combination.
Each of these factors is discussed below.
In the proposed listing rule (80 FR 55304; September 15, 2015), we
carefully assessed the best scientific and commercial information
available regarding the past, present, and future threats to the white
fringeless orchid and provided a detailed account of those threats and
the biological status of white fringeless orchid.
We have determined that the threats to white fringeless orchid
consist primarily of destruction and modification of habitat (Factor A)
resulting in excessive shading, soil disturbance, altered hydrology,
and proliferation of invasive plant species; collecting for
recreational or commercial purposes (Factor B); herbivory (Factor C);
and small population sizes and dependence on specific pollinators and
fungi to complete its life cycle (Factor E). Existing regulatory
mechanisms have not led to a reduction or removal of threats posed to
the species from these factors (Factor D). We summarize each of those
threats here. Please refer to the proposed listing rule (80 FR 55304;
September 15, 2015) for the full discussion.
Habitat destruction and modification (Factor A) from development,
silvicultural practices, excessive shading, and altered hydrology
(i.e., pond construction, beaver dam removal) have resulted in
extirpation of the species from 10 sites (Shea 1992, pp. 15, 25; TDEC
2014). These threats, in addition to invasive plant species (U.S.
Forest Service (USFS) 2008, p. 53; Richards 2013, pers. comm.; KSNPC
2014; TDEC 2014), feral hogs (Zettler 1994, p. 687; USFS 2008, p. 54;
Richards 2013, pers. comm.; Richards 2014, pers. comm.; Tackett 2015,
pers. comm.), and right-of-way maintenance (Taylor 2014, pers. comm.),
are associated with habitat modifications affecting dozens of other
occurrences that are extant or of uncertain status. The best available
information indicates that habitat for many existing populations is
adversely affected by factors that either directly harm individual
white fringeless orchids or alter the plant communities, soils, and
water flow in the sites where they occur. These factors include
residential development, utility and road right-of-way maintenance,
timber harvesting, invasive species encroachment, and vegetation
succession in the absence of disturbance. Impacts to habitat from
activities such as development and silvicultural practices include
direct impacts such as habitat conversion and ground disturbance, and
indirect impacts such as altered hydrology, increased shading, and
introduction of invasive, nonnative plants. The threats to the white
fringeless orchid from habitat destruction and modification are
occurring throughout much of the species' range and these population-
level impacts are expected to continue into the foreseeable future.
During the comment period, GDOT and Georgia Power provided
information on conservation efforts that have been directed to a
roadside occurrence in Chattooga County, Georgia, which is located in a
power transmission right-of-way. As noted in the proposed listing rule
(80 FR 55304; September 15, 2015), this site was adversely affected by
unauthorized collection in 2004, and remains vulnerable to this threat
due to its location alongside a State highway. Georgia Power and GDOT
have designated this site an ``Environmentally Sensitive Area,''
restricting mowing and herbicide use. They are also working with ABG to
augment the population at this occurrence with plants propagated from
seed collected at this site. Georgia Power is also collaborating with
GDNR to protect, monitor, and manage another occurrence, located in
Rabun County, Georgia, and reported that a prescribed burn was recently
conducted in the area where this occurrence is located. ABG staff have
collected seeds from this population to produce propagated plants that
will be used to augment the population at this occurrence.
Collecting for scientific, recreational, or commercial purposes
(Factor B) has been determined to be the cause for extirpation of the
white fringeless orchid at its type locality (Ettman and McAdoo 1979
cited in Zettler and Fairey 1990, p. 212), and recent evidence
demonstrates that collection remains a threat to this species. Fungal
pathogens have been identified as a threat to white fringeless orchid,
but a threat with potentially greater impact associated with Factor C
is inflorescence herbivory, presumably by deer (Zettler and Fairey
1990, p. 212-214). Flower herbivory has been reported at over one-third
of extant occurrences and likely is a factor threatening most white
fringeless orchid occurrences (Shea 1992, pp. 27, 61, 71-77, 95-97;
TDEC 2012, p. 3; KSNPC 2014; TDEC 2014), especially where low numbers
of plants are present. Tuber herbivory or soil disturbance by feral
hogs has been reported at multiple occurrences, including the site
harboring the largest known white fringeless orchid population (Zettler
1994, p. 687; USFS 2008, p. 54).
The effects of all of the above-described threats are intensified
by the small population sizes that characterize a majority of
occurrences throughout the species' geographic range (Factor E), due to
their diminished capacity to recover from loss of individuals or low
[[Page 62831]]
reproductive output resulting from other threats (Zettler et al. 1996,
p. 22). Further, the species' dependence on a limited number of
Lepidoptera (Zettler et al. 1996, p. 16) and a single species of fungi
(Currah et al. 1997, p. 30) to complete its life cycle make it
vulnerable to disturbances that diminish habitat suitability for these
taxa as well (Factor E). Climate has changed in recent decades in the
southeastern United States, and the rate of change likely will continue
to increase into the future (Karl et al. 2009, pp. 111-112) (Factor E).
Although we do not have data to determine specifically how the habitats
where the white fringeless orchid occurs will be affected by, or how
the species will respond to, these changes, the potential for adverse
effects to the white fringeless orchid, either through changes in
habitat suitability or effects on populations of pollinators or
mycorrhizal fungi, is likely to increase as climate continues to change
at an accelerating rate.
Determination
Section 4 of the Act (16 U.S.C. 1533), and its implementing
regulations at 50 CFR part 424, set forth the procedures for adding
species to the Federal Lists of Endangered and Threatened Wildlife and
Plants. 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 white fringeless orchid
is likely to become endangered throughout all or a significant portion
of its range within the foreseeable future based on the low to moderate
threats currently impacting the species. The species is known to be
extant at 57 locations (see Table 1, above), but low numbers of
individuals have been observed at more than half of these (see Figure 1
in the proposed listing rule: 80 FR 55304, September 15, 2015, p.
55309), distributed across the species' range, and their persistence
into the future is uncertain. Furthermore, the threats of habitat
destruction or modification and herbivory are present throughout the
species' geographic range. Left unmanaged, these threats will likely
lead to further reductions in the species' geographic range and
abundance at individual sites, increasing the risk of extinction to the
point of endangerment. The combination of small population sizes
combined with the white fringeless orchid's dependence on specific
pollinators and fungi to complete its life cycle diminishes the
resilience of populations to recover from adverse effects of threats
due to habitat destruction or modification and herbivory.
Therefore, on the basis of the best available scientific and
commercial information, we are listing the white fringeless orchid as
threatened in accordance with sections 3(20) and 4(a)(1) of the Act.
The species does not currently meet the definition of endangered
species, because a sufficient number of robust populations are present
on publicly owned or managed lands, which despite numerous threats, are
actively managed such that the risk of extinction is not imminent.
Furthermore, conservation efforts have been initiated that could be
effective in reducing threats by increasing population sizes and
improving habitat conditions across much of the species' geographic
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
white fringeless orchid 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).
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 requires that recovery actions be carried out for all 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 requires 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. The recovery plan identifies site-specific
management actions that set a trigger for review of the five factors
that control whether a species remains endangered or may be downlisted
or delisted, 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. Revisions of the plan may be done to address continuing
or new threats to the species, as new substantive information becomes
available. Recovery teams (composed of species experts, Federal and
State agencies, nongovernmental organizations, and stakeholders) are
often established to develop recovery plans. When completed, the
recovery outline, draft recovery plan, and the final recovery plan will
be available on our Web site (https://www.fws.gov/endangered) or from
our Tennessee Ecological Services Field Office (see FOR FURTHER
INFORMATION CONTACT).
Implementation of recovery actions generally requires the
participation of a broad range of partners, including other Federal
agencies, States, Tribes, nongovernmental organizations, businesses,
and private landowners. Examples of recovery actions include habitat
restoration (e.g., restoration of native vegetation), research, captive
propagation and reintroduction, and outreach and education. The
recovery of many listed species cannot be accomplished solely on
Federal lands because their 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.
Following publication of this final listing rule, 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
[[Page 62832]]
organizations. In addition, pursuant to section 6 of the Act, the
States of Georgia, South Carolina, Alabama, Mississippi, and Tennessee
and the Commonwealth of Kentucky will be eligible for Federal funds to
implement management actions that promote the protection or recovery of
the white fringeless orchid. Information on our grant programs that are
available to aid species recovery can be found at: https://www.fws.gov/grants.
Please let us know if you are interested in participating in
recovery efforts for the white fringeless orchid. Additionally, we
invite you to submit any new information on this species whenever it
becomes available and any information you may have for recovery
planning purposes (see FOR FURTHER INFORMATION CONTACT).
Section 7(a) of the Act requires Federal agencies to evaluate their
actions with respect to any species that is 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)(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 any endangered or threatened 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
consultation, as described in the preceding paragraph, include
management and any other landscape-altering activities on Federal lands
administered by the U.S. Fish and Wildlife Service, U.S. Forest Service
(USFS), and National Park Service (NPS); issuance of section 404 Clean
Water Act (33 U.S.C. 1251 et seq.) permits by the U.S. Army Corps of
Engineers; powerline right-of-way construction and maintenance by the
TVA; and construction and maintenance of roads or highways by the
Federal Highway Administration.
The Act and its implementing regulations set forth a series of
general prohibitions and exceptions that apply to endangered and
threatened plants. With regard to threatened plants, 50 CFR 17.71
provides that all of the prohibitions in 50 CFR 17.61 applicable to
endangered plants apply to threatened plants, with one exception. Thus,
the regulations at 50 CFR 17.71(a) make it illegal for any person
subject to the jurisdiction of the United States to import or export,
transport in interstate or foreign commerce in the course of a
commercial activity, sell or offer for sale in interstate or foreign
commerce, or remove and reduce the species to possession from areas
under Federal jurisdiction any threatened plant. There is an exception
for the seeds of cultivated specimens, provided that a statement that
the seeds are of ``cultivated origin'' accompanies the seeds or their
container. The Act itself, at 16 U.S.C. 1538(a)(2)(B), prohibits
malicious damage or destruction of any such species on any area under
Federal jurisdiction, and the removal, cutting, digging up, or damaging
or destroying of any such species on any other area in knowing
violation of any State law or regulation, or in the course of any
violation of a State criminal trespass law.
Under 50 CFR 17.72, we may issue permits to carry out otherwise
prohibited activities involving threatened plants under certain
circumstances. A permit issued under this section must be for one of
the following: Scientific purposes, the enhancement of the propagation
or survival of threatened species, economic hardship, botanical or
horticultural exhibition, educational purposes, or other activities
consistent with the purposes and policy 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 final listing
on proposed and ongoing activities within the range of a listed
species. 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:
(1) Unauthorized collecting, handling, possessing, selling,
delivering, carrying, or transporting of white fringeless orchid,
including interstate transportation across State lines and import or
export across international boundaries, except for properly documented
antique specimens of this species at least 100 years old, as defined by
section 10(h)(1) of the Act;
(2) Unauthorized removal, damage, or destruction of white
fringeless orchid plants from populations located on Federal land
(USFS, NPS, and Service lands); and
(3) Unauthorized removal, damage, or destruction of white
fringeless orchid plants on private land in violation of any State
regulation, including criminal trespass.
At this time, we are unable to identify specific activities that
would not be considered to result in a violation of section 9 of the
Act because the white fringeless orchid occurs in a variety of habitat
conditions across its range and it is likely that site-specific
conservation measures may be needed for activities that may directly or
indirectly affect the species. Questions regarding whether specific
activities would constitute a violation of section 9 of the Act should
be directed to the Tennessee Ecological Services Field Office (see FOR
FURTHER INFORMATION CONTACT).
Required Determinations
National Environmental Policy Act (42 U.S.C. 4321 et seq.)
We have determined that environmental assessments and environmental
impact statements, as defined under the authority of the National
Environmental Policy Act, need not be prepared in connection with
listing a species as an endangered or threatened species under the
Endangered Species Act. We published a notice outlining our reasons for
this determination in the Federal Register on October 25, 1983 (48 FR
49244).
References Cited
A complete list of references cited in this rulemaking is available
on the Internet at https://www.regulations.gov and upon request from the
Tennessee Ecological Services Field Office (see FOR FURTHER INFORMATION
CONTACT).
Authors
The primary authors of this final rule are the staff members of the
Tennessee Ecological Services Field Office.
List of Subjects in 50 CFR Part 17
Endangered and threatened species, Exports, Imports, Reporting and
recordkeeping requirements, Transportation.
Regulation Promulgation
Accordingly, we amend part 17, subchapter B of chapter I, title 50
of the Code of Federal Regulations, as follows:
PART 17--ENDANGERED AND THREATENED WILDLIFE AND PLANTS
0
1. The authority citation for part 17 continues to read as follows:
Authority: 16 U.S.C. 1361-1407; 1531-1544; and 4201-4245, unless
otherwise noted.
0
2. Amend Sec. 17.12(h) by adding an entry for ``Platanthera
integrilabia'' to the List of Endangered and Threatened
[[Page 62833]]
Plants in alphabetical order under FLOWERING PLANTS to read as follows:
Sec. 17.12 Endangered and threatened plants.
* * * * *
(h) * * *
----------------------------------------------------------------------------------------------------------------
Listing citations and
Scientific name Common name Where listed Status applicable rules
----------------------------------------------------------------------------------------------------------------
Flowering Plants
* * * * * * *
Platanthera integrilabia........ White fringeless Wherever found.... T 81 FR [Insert Federal
orchid. Register page where
the document begins];
September 13, 2016.
* * * * * * *
----------------------------------------------------------------------------------------------------------------
Dated: August 23, 2016.
James W. Kurth,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2016-21954 Filed 9-12-16; 8:45 am]
BILLING CODE 4333-15-P