# 80 FR 61030: Endangered and Threatened Wildlife and Plants; Designation of Critical Habitat for Kentucky Arrow Darter

> Federal · Regulations · In force

URL: https://www.frixlaw.com/law-library/statutes/FR_PRORULE_2015-25290

## Section

- **Citation:** 80 FR 61030
- **Heading:** Endangered and Threatened Wildlife and Plants; Designation of Critical Habitat for Kentucky Arrow Darter
- **Jurisdiction:** Federal
- **Kind:** Regulations
- **Status:** In force
- **Text as of:** August 14, 2026
- **Source:** Compiled text
- **Location:** Federal Register / Vol. 80 / 80 FR 61030

## Text

DEPARTMENT OF THE INTERIOR Fish and Wildlife Service 50 CFR Part 17 [Docket No. FWS-R4-ES-2015-0133; 4500030113] RIN 1018-BB05 Endangered and Threatened Wildlife and Plants; Designation of Critical Habitat for Kentucky Arrow Darter AGENCY:
Fish and Wildlife Service, Interior.

ACTION:
Proposed rule.

SUMMARY:
We, the U.S. Fish and Wildlife Service (Service), propose to designate critical habitat for the Kentucky arrow darter ( Etheostoma spilotum ) under the Endangered Species Act (Act). In total, approximately 395 stream kilometers (skm) (246 stream miles (smi)) are being proposed for designation of critical habitat for the Kentucky arrow darter in Breathitt, Clay, Harlan, Jackson, Knott, Lee, Leslie, Owsley, Perry, and Wolfe Counties, Kentucky. If we finalize this rule as proposed, it would extend the Act's protections to this species' critical habitat. We also announce the availability of our draft economic analysis of the proposed designation.

DATES:
We will accept comments on the proposed rule or draft economic analysis that are received or postmarked on or before December 7, 2015. Comments submitted electronically using the Federal eRulemaking Portal (see ADDRESSES , below) must be received by 11:59 p.m. Eastern Time on the closing date. We must receive requests for public hearings, in writing, at the address shown in FOR FURTHER INFORMATION CONTACT by November 23, 2015.

ADDRESSES:
Written comments: You may submit comments on the proposed rule or draft economic analysis by one of the following methods:
(1) Electronically: Go to the Federal eRulemaking Portal: http://www.regulations.gov. In the Search box, enter Docket No. FWS-R4-ES-2015-0133, which is the docket number for this rulemaking. Then, in the Search panel on the left side of the screen, under the Document Type heading, click on the Proposed Rules link to locate this document. You may submit a comment by clicking on “Comment Now!”
s:
(1) Electronically: Go to the Federal eRulemaking Portal: http://www.regulations.gov. In the Search box, enter Docket No. FWS-R4-ES-2015-0133, which is the docket number for this rulemaking. Then, in the Search panel on the left side of the screen, under the Document Type heading, click on the Proposed Rules link to locate this document. You may submit a comment by clicking on “Comment Now!”
(2) By hard copy: Submit by U.S. mail or hand-delivery to: Public Comments Processing, Attn: FWS-R4-ES-2015-0133; U.S. Fish and Wildlife Service, MS: BPHC, 5275 Leesburg Pike, Falls Church, VA 22041-3803.
We request that you send comments only by the methods described above. We will post all comments on http://www.regulations.gov. This generally means that we will post any personal information you provide us (see Information Requested, below, for more information).
Document availability: The draft economic analysis is available at http://www.fws.gov/frankfort/, at http://www.regulations.gov at Docket No. FWS-R4-ES-2015-0133, and at the Kentucky Ecological Services Field Office (see FOR FURTHER INFORMATION CONTACT ).
The coordinates, plot points, or both from which the maps are generated are included in the administrative record for this critical habitat designation and are available at http://www.fws.gov/frankfort/, at http://www.regulations.gov at Docket No. FWS-R4-ES-2015-0133, and at the Kentucky Ecological Services Field Office) (see FOR FURTHER INFORMATION CONTACT ). Any additional tools or supporting information that we may develop for this critical habitat designation will also be available at the Fish and Wildlife Service Web site and Field Office set out above, and may also be included in this rule or at http://www.regulations.gov.
FOR FURTHER INFORMATION CONTACT:
Virgil Lee Andrews, Jr., Field Supervisor, U.S. Fish and Wildlife Service, Kentucky Ecological Services Field Office, 330 West Broadway, Suite 265, Frankfort, KY 40601; telephone 502-695-0468, x108; facsimile 502-695-1024
he Fish and Wildlife Service Web site and Field Office set out above, and may also be included in this rule or at http://www.regulations.gov.
FOR FURTHER INFORMATION CONTACT:
Virgil Lee Andrews, Jr., Field Supervisor, U.S. Fish and Wildlife Service, Kentucky Ecological Services Field Office, 330 West Broadway, Suite 265, Frankfort, KY 40601; telephone 502-695-0468, x108; facsimile 502-695-1024. If you use a telecommunications device for the deaf (TDD), call the Federal Information Relay Service (FIRS) at 800-877-8339.

SUPPLEMENTARY INFORMATION:
Executive Summary
Why we need to publish a rule. Under the Endangered Species Act, when we determine that a species is threatened or endangered, we must designate critical habitat to the maximum extent prudent and determinable. Designations of critical habitat can only be completed by issuing a rule.
This document consists of a proposed rule to designate critical habitat for the Kentucky arrow darter. Elsewhere in today's Federal Register , we propose to list the Kentucky arrow darter as a threatened species under the Act.
The basis for our action. Section 4(a)(3) of the Act requires the Secretary to designate critical habitat, to the maximum extent prudent and determinable, for an endangered or threatened species at the time it is listed. Section 4(b)(2) of the Act states that the Secretary shall designate and make revisions to critical habitat on the basis of the best available scientific data after taking into consideration the economic impact, national security impact, and any other relevant impact of specifying any particular area as critical habitat. The Secretary may exclude an area from critical habitat if she determines that the benefits of such exclusion outweigh the benefits of specifying such area as part of the critical habitat, unless she determines, based on the best scientific data available, that the failure to designate such area as critical habitat will result in the extinction of the species
y particular area as critical habitat. The Secretary may exclude an area from critical habitat if she determines that the benefits of such exclusion outweigh the benefits of specifying such area as part of the critical habitat, unless she determines, based on the best scientific data available, that the failure to designate such area as critical habitat will result in the extinction of the species. We have determined that designating critical habitat is both prudent and determinable, and we propose a total of approximately 395 skm (246 smi) of critical habitat in eastern Kentucky.
We prepared a draft economic analysis of the proposed designation of critical habitat. In order to consider economic impacts, we have prepared a draft economic analysis of the proposed critical habitat designation and related factors.
We will seek peer review. We are seeking comments from independent specialists to ensure that this critical habitat proposal is based on scientifically sound data and analyses. We have invited these peer reviewers to comment on our specific assumptions and conclusions in this proposal to designate critical habitat. Because we will consider all comments and information we receive during the comment period, our final designation may differ from this proposal.
Information Requested
We intend that any final action resulting from this proposed rule will be based on the best scientific and commercial data available and be as accurate and effective as possible. Therefore, we request comments or information from other concerned government agencies, Native American tribes, the scientific community, industry, or any other interested party concerning this proposed rule. We particularly seek comments concerning:
n resulting from this proposed rule will be based on the best scientific and commercial data available and be as accurate and effective as possible. Therefore, we request comments or information from other concerned government agencies, Native American tribes, the scientific community, industry, or any other interested party concerning this proposed rule. We particularly seek comments concerning:
(1) The reasons why we should or should not designate habitat as “critical habitat” under section 4 of the Act (16 U.S.C. 1531 et seq. ) including whether there are threats to the species from human activity, the degree of which can be expected to increase due to the designation, and whether that increase in threat outweighs the benefit of designation such that the designation of critical habitat may not be prudent.
(2) Specific information on:
(a) The amount and distribution of Kentucky arrow darter habitat;
(b) What areas, that were occupied at the time of listing ( i.e., are currently occupied) and that contain features essential to the conservation of the species, should be included in the designation and why;
(c) Special management considerations or protection that may be needed in critical habitat areas we are proposing, including managing for the potential effects of climate change; and
(d) What areas not occupied at the time of listing are essential for the conservation of the species and why.
(3) Land use designations and current or planned activities in the subject areas and their possible impacts on proposed critical habitat.
(4) Information on the projected and reasonably likely impacts of climate change on the Kentucky arrow darter and proposed critical habitat.
(5) Any probable economic, national security, or other relevant impacts of designating any area that may be included in the final designation, and the benefits of including or excluding areas that exhibit these impacts.
acts on proposed critical habitat.
(4) Information on the projected and reasonably likely impacts of climate change on the Kentucky arrow darter and proposed critical habitat.
(5) Any probable economic, national security, or other relevant impacts of designating any area that may be included in the final designation, and the benefits of including or excluding areas that exhibit these impacts.
(6) Information on the extent to which the description of economic impacts in the draft economic analysis (DEA) is a reasonable estimate of the likely economic impacts.
(7) The likelihood of adverse social reactions to the designation of critical habitat, as discussed in the associated documents of the draft economic analysis, and how the consequences of such reactions, if likely to occur, would relate to the conservation and regulatory benefits of the proposed critical habitat designation.
(8) Whether any specific areas we are proposing for critical habitat designation should be considered for exclusion under section 4(b)(2) of the Act, and whether the benefits of potentially excluding any specific area outweigh the benefits of including that area under section 4(b)(2) of the Act.
(9) Whether we could improve or modify our approach to designating critical habitat in any way to provide for greater public participation and understanding, or to better accommodate public concerns and comments.
You may submit your comments and materials concerning this proposed rule by one of the methods listed in ADDRESSES . We request that you send comments only by the methods described in ADDRESSES .
All comments submitted electronically via http://www.regulations.gov will be presented on the Web site in their entirety as submitted. For comments submitted via hard copy, we will post your entire comment—including your personal identifying information—on http://www.regulations.gov
f the methods listed in ADDRESSES . We request that you send comments only by the methods described in ADDRESSES .
All comments submitted electronically via http://www.regulations.gov will be presented on the Web site in their entirety as submitted. For comments submitted via hard copy, we will post your entire comment—including your personal identifying information—on http://www.regulations.gov. You may request at the top of your document that we withhold personal information such as your street address, phone number, or email address from public review; however, we cannot guarantee that we will be able to do so.
Comments and materials we receive, as well as supporting documentation we used in preparing this proposed rule, will be available for public inspection on http://www.regulations.gov, or by appointment, during normal business hours, at the U.S. Fish and Wildlife Service, Kentucky Ecological Services Field Office (see FOR FURTHER INFORMATION CONTACT ).
Previous Federal Actions
All previous Federal actions are described in the proposal to list the Kentucky arrow darter as a threatened species under the Act, which is published elsewhere in today's Federal Register.
Critical Habitat
Background
Critical habitat is defined in section 3 of the Act as:
(1) The specific areas within the geographical area occupied by the species, at the time it is listed in accordance with the Act, on which are found those physical or biological features:
(a) Essential to the conservation of the species, and
Act, which is published elsewhere in today's Federal Register.
Critical Habitat
Background
Critical habitat is defined in section 3 of the Act as:
(1) The specific areas within the geographical area occupied by the species, at the time it is listed in accordance with the Act, on which are found those physical or biological features:
(a) Essential to the conservation of the species, and
(b) Which may require special management considerations or protection; and
(2) Specific areas outside the geographical area occupied by the species at the time it is listed, upon a determination that such areas are essential for the conservation of the species.
Conservation, as defined under section 3 of the Act, means to use and the use of all methods and procedures that are necessary to bring an endangered or threatened species to the point at which the measures provided pursuant to the Act are no longer necessary. Such methods and procedures include, but are not limited to, all activities associated with scientific resources management such as research, census, law enforcement, habitat acquisition and maintenance, propagation, live trapping, and transplantation, and, in the extraordinary case where population pressures within a given ecosystem cannot be otherwise relieved, may include regulated taking.
Critical habitat receives protection under section 7 of the Act through the requirement that Federal agencies ensure, in consultation with the Service, that any action they authorize, fund, or carry out is not likely to result in the destruction or adverse modification of critical habitat. The designation of critical habitat does not affect land ownership or establish a refuge, wilderness, reserve, preserve, or other conservation area. Such designation does not allow the government or public to access private lands. Such designation does not require implementation of restoration, recovery, or enhancement measures by non-Federal landowners
or adverse modification of critical habitat. The designation of critical habitat does not affect land ownership or establish a refuge, wilderness, reserve, preserve, or other conservation area. Such designation does not allow the government or public to access private lands. Such designation does not require implementation of restoration, recovery, or enhancement measures by non-Federal landowners. Where a landowner requests Federal agency funding or authorization for an action that may affect a listed species or critical habitat, the consultation requirements of section 7(a)(2) of the Act would apply, but even in the event of a destruction or adverse modification finding, the obligation of the Federal action agency and the landowner is not to restore or recover the species, but to implement reasonable and prudent alternatives to avoid destruction or adverse modification of critical habitat.
Under the first prong of the Act's definition of critical habitat, areas within the geographical area occupied by the species at the time it was listed are included in a critical habitat designation if they contain physical or biological features (1) which are essential to the conservation of the species and (2) which may require special management considerations or protection. For these areas, critical habitat designations identify, to the extent known using the best scientific and commercial data available, those physical or biological features that are essential to the conservation of the species (such as space, food, cover, and protected habitat). In identifying those physical and biological features within an area, we focus on the principal biological or physical constituent elements (primary constituent elements such as roost sites, nesting grounds, seasonal wetlands, water quality, tide, soil type) that are essential to the conservation of the species
to the conservation of the species (such as space, food, cover, and protected habitat). In identifying those physical and biological features within an area, we focus on the principal biological or physical constituent elements (primary constituent elements such as roost sites, nesting grounds, seasonal wetlands, water quality, tide, soil type) that are essential to the conservation of the species. Primary constituent elements are those specific elements of the physical or biological features that provide for a species' life-history processes and are essential to the conservation of the species.
Under the second prong of the Act's definition of critical habitat, we can designate critical habitat in areas outside the geographical area occupied
Section 4 of the Act requires that we designate critical habitat on the basis of the best scientific data available. Further, our Policy on Information Standards Under the Endangered Species Act (published in the Federal Register on July 1, 1994 (59 FR 34271)), the Information Quality Act (section 515 of the Treasury and General Government Appropriations Act for Fiscal Year 2001 (Pub. L. 106-554; H.R. 5658)), and our associated Information Quality Guidelines, provide criteria, establish procedures, and provide guidance to ensure that our decisions are based on the best scientific data available. They require our biologists, to the extent consistent with the Act and with the use of the best scientific data available, to use primary and original sources of information as the basis for recommendations to designate critical habitat.
When we are determining which areas should be designated as critical habitat, our primary source of information is generally the information developed during the listing process for the species
he extent consistent with the Act and with the use of the best scientific data available, to use primary and original sources of information as the basis for recommendations to designate critical habitat.
When we are determining which areas should be designated as critical habitat, our primary source of information is generally the information developed during the listing process for the species. Additional information sources may include the recovery plan for the species, articles in peer-reviewed journals, conservation plans developed by States and counties, scientific status surveys and studies, biological assessments, other unpublished materials, or experts' opinions or personal knowledge.
Habitat is dynamic, and species may move from one area to another over time. We recognize that critical habitat designated at a particular point in time may not include all of the habitat areas that we may later determine are necessary for the recovery of the species. For these reasons, a critical habitat designation does not signal that habitat outside the designated area is unimportant or may not be needed for recovery of the species. Areas that are important to the conservation of the listed species, both inside and outside the critical habitat designation, will continue to be subject to: (1) Conservation actions implemented under section 7(a)(1) of the Act, (2) regulatory protections afforded by the requirement in section 7(a)(2) of the Act for Federal agencies to ensure their actions are not likely to jeopardize the continued existence of any endangered or threatened species, and (3) section 9 of the Act's prohibitions on taking any individual of the species, including taking caused by actions that affect habitat. Federally funded or permitted projects affecting listed species outside their designated critical habitat areas may still result in jeopardy findings in some cases. If we list the Kentucky arrow darter, these protections and conservation tools would continue to contribute to recovery of this species
ns on taking any individual of the species, including taking caused by actions that affect habitat. Federally funded or permitted projects affecting listed species outside their designated critical habitat areas may still result in jeopardy findings in some cases. If we list the Kentucky arrow darter, these protections and conservation tools would continue to contribute to recovery of this species. Similarly, critical habitat designations made on the basis of the best available information at the time of designation will not control the direction and substance of future recovery plans, habitat conservation plans (HCPs), or other species conservation planning efforts if new information available at the time of these planning efforts calls for a different outcome.
Prudency Determination
Section 4(a)(3) of the Act, as amended, and implementing regulations (50 CFR 424.12), require that, to the maximum extent prudent and determinable, the Secretary shall designate critical habitat at the time the species is determined to be an endangered or threatened species. Our regulations (50 CFR 424.12(a)(1)) state that the designation of critical habitat is not prudent when one or both of the following situations exist:
(1) The species is threatened by taking or other human activity, and identification of critical habitat can be expected to increase the degree of threat to the species, or
(2) Such designation of critical habitat would not be beneficial to the species.
As discussed in the proposed listing rule, there is currently no imminent threat of take attributed to collection or vandalism (listing factor B) for this species, and identification and mapping of critical habitat is not expected to initiate any such threat. In the absence of finding that the designation of critical habitat would increase threats to a species, if there are any benefits to a critical habitat designation, then a prudent finding is warranted
y no imminent threat of take attributed to collection or vandalism (listing factor B) for this species, and identification and mapping of critical habitat is not expected to initiate any such threat. In the absence of finding that the designation of critical habitat would increase threats to a species, if there are any benefits to a critical habitat designation, then a prudent finding is warranted. Here, the potential benefits of designation include: (1) Triggering consultation under section 7 of the Act, in areas for actions in which there may be a Federal nexus where it would not otherwise occur because, for example, it is or has become unoccupied or the occupancy is in question; (2) focusing conservation activities on the most essential features and areas; (3) providing educational benefits to State or county governments or private entities; and (4) reducing the potential for people to cause inadvertent harm to the species. Because we have determined that the designation of critical habitat will not likely increase the degree of threat to the species and may provide some measure of benefit, we find that designation of critical habitat is prudent for the Kentucky arrow darter.
Critical Habitat Determinability
Having determined that designation is prudent under section 4(a)(3) of the Act, we must find whether critical habitat for the Kentucky arrow darter is determinable. Our regulations at 50 CFR 424.12(a)(2) state that critical habitat is not determinable when one or both of the following situations exist:
critical habitat is prudent for the Kentucky arrow darter.
Critical Habitat Determinability
Having determined that designation is prudent under section 4(a)(3) of the Act, we must find whether critical habitat for the Kentucky arrow darter is determinable. Our regulations at 50 CFR 424.12(a)(2) state that critical habitat is not determinable when one or both of the following situations exist:
(i) Information sufficient to perform required analyses of the impacts of the designation is lacking, or
(ii) The biological needs of the species are not sufficiently well known to permit identification of an area as critical habitat.
When critical habitat is not determinable, the Act allows the Service an additional year to publish a critical habitat designation (16 U.S.C. 1533(b)(6)(C)(ii)).
We have reviewed the available information pertaining to the biological needs of the species and characteristics of the species' habitat. This and other information represent the best scientific data available and led us to conclude that the designation of critical habitat is determinable for the Kentucky arrow darter.
Physical or Biological Features
In accordance with section 3(5)(A)(i) of the Act and regulations at 50 CFR 424.12(b), in determining which areas within the geographical area occupied by the species at the time of listing to designate as critical habitat, we consider the physical or biological features that are essential to the conservation of the species and which may require special management considerations or protection. These include, but are not limited to:
(1) Space for individual and population growth and for normal behavior;
(2) Food, water, air, light, minerals, or other nutritional or physiological requirements;
(3) Cover or shelter;
(4) Sites for breeding, reproduction, or rearing (or development) of offspring; and
the species and which may require special management considerations or protection. These include, but are not limited to:
(1) Space for individual and population growth and for normal behavior;
(2) Food, water, air, light, minerals, or other nutritional or physiological requirements;
(3) Cover or shelter;
(4) Sites for breeding, reproduction, or rearing (or development) of offspring; and
(5) Habitats that are protected from disturbance or are representative of the historic, geographical, and ecological distributions of a species.
We derive the specific physical or biological features essential for the Kentucky arrow darter from studies of its habitat, ecology, and life history as described below. Additional information can be found in the proposed listing rule published elsewhere in today's Federal Register . To identify the physical or biological features essential to the conservation of the species, we have relied on current conditions at locations where the species survives, the limited information available on the species and its closest relatives, and factors associated with the decline of other fishes that occupy similar habitats in the Southeast. We have determined that the following physical or biological features are essential to the Kentucky arrow darter.
Space for Individual and Population Growth and for Normal Behavior
Little is known about the specific space requirements of the Kentucky arrow darter; however, the species is typically observed in moderate- to high-gradient, first- to third-order, geomorphically stable streams (Lotrich 1973, p. 382; Thomas 2008, p. 6). Geomorphically stable streams transport sediment while maintaining their horizontal and vertical dimensions (width to depth ratio and cross-sectional area), pattern (sinuosity), and longitudinal profile (riffles, runs, and pools), thereby conserving the physical characteristics of the stream, including bottom features such as riffles, runs, and pools and the transition zones between these features (Rosgen 1996, p. 1-3)
streams transport sediment while maintaining their horizontal and vertical dimensions (width to depth ratio and cross-sectional area), pattern (sinuosity), and longitudinal profile (riffles, runs, and pools), thereby conserving the physical characteristics of the stream, including bottom features such as riffles, runs, and pools and the transition zones between these features (Rosgen 1996, p. 1-3). The protection and maintenance of these habitat features accommodate spawning, rearing, growth, migration, and other normal behaviors of the species.
During most of the year (late spring through winter), Kentucky arrow darters occupy shallow pools between 10-45 centimeters (cm) (4-18 inches (in)) or transitional areas between riffles and pools (runs and glides) with cobble and boulder substrates that are interspersed with clean (relatively silt free) sand and gravel (Lotrich 1973, p. 382; Thomas 2008, p. 6). Most individuals are encountered near some type of instream cover: Large cobble, boulders, bedrock ledges, or woody debris piles (Thomas 2008, p. 6). During the spawning period (April through June), Kentucky arrow darters utilize riffle habitats with relatively silt free, gravel, cobble, and sand substrates (Kuehne and Barbour 1983, p. 71). Streams inhabitated by Kentucky arrow darters tend to be clear and cool (generally less than or equal to 24 degrees Celsius (°C) (72 degrees Fahrenheit (°F))), with shaded corridors and naturally vegetated, intact riparian zones (Lotrich 1973, p. 378; Thomas 2008, pp. 7, 23).
Limited information exists about upstream or downstream movements of Kentucky arrow darters; however, there is evidence that the species can utilize relatively long stream reaches. Observations by Lowe (1979, pp
an or equal to 24 degrees Celsius (°C) (72 degrees Fahrenheit (°F))), with shaded corridors and naturally vegetated, intact riparian zones (Lotrich 1973, p. 378; Thomas 2008, pp. 7, 23).
Limited information exists about upstream or downstream movements of Kentucky arrow darters; however, there is evidence that the species can utilize relatively long stream reaches. Observations by Lowe (1979, pp. 26-27) of potential dispersal behavior for a related species (the Cumberland arrow darter ( Etheostoma sagitta )) in Tennessee, preliminary findings from a movement study at Eastern Kentucky University (EKU), and recent survey results by Kentucky Department of Fish and Wildlife Resources (KDFWR) suggest that Kentucky arrow darters can utilize stream reaches of over 4 skm (2.5 smi) and disperse to other tributaries (Baxter 2014, pers. comm.; Thomas 2015, pers. comm.) (see “Habitat and Life History” section of our proposed listing rule published elsewhere in today's Federal Register ).
The current range of the Kentucky arrow darter has been reduced from 74 historically occupied streams to 47 currently occupied streams due to destruction, modification, and fragmentation of habitat. Fragmentation of the species' habitat has subjected these small populations to genetic isolation, reduced space for rearing and reproduction, reduced adaptive capabilities, and an increased likelihood of local extinctions (Burkhead et al. 1997, pp. 397-399; Hallerman 2003, pp. 363-364). Genetic variation and diversity within a species are essential to recovery, adaptation to environmental change, and long-term viability (capability to live, reproduce, and develop) (Noss and Cooperrider 1994, pp. 282-297; Harris 1984, pp. 93-107; Fluker et al. 2007, p. 2). The long-term viability of a species is founded on the conservation of numerous local populations throughout its geographic range (Harris 1984, pp. 93-104)
ty within a species are essential to recovery, adaptation to environmental change, and long-term viability (capability to live, reproduce, and develop) (Noss and Cooperrider 1994, pp. 282-297; Harris 1984, pp. 93-107; Fluker et al. 2007, p. 2). The long-term viability of a species is founded on the conservation of numerous local populations throughout its geographic range (Harris 1984, pp. 93-104). Connectivity of these habitats is essential in preventing further fragmentation and isolation of Kentucky arrow darter populations and promoting species movement and genetic flow between populations.
Therefore, based on the information above, we identify shallow pools, runs, glides, and riffles and associated stream segments of geomorphically stable, first- to third-order streams to be physical or biological features essential to the conservation of the Kentucky arrow darter. The maintenance of these habitats is essential in accommodating feeding, breeding, growth, and other normal behaviors of the Kentucky arrow darter and in promoting gene flow within the species.
Food, Water, Air, Light, Minerals, or Other Nutritional or Physiological Requirements
Feeding habits of the Kentucky arrow darter were documented by Lotrich (1973, pp. 380-382) in the Clemons Fork system, Breathitt County, Kentucky. The primary prey item was mayflies (Order Ephemeroptera), which comprised 77 percent of identifiable food items (420 of 542 items) in 57 Kentucky arrow darter stomachs (Lotrich 1973, p. 381). Large Kentucky arrow darters (greater than 70 millimeters (mm) (2.8 in) total length (TL)) utilized small crayfishes, as 7 of 8 stomachs examined by Lotrich (1973, p. 381) contained crayfishes ranging in size from 11 to 24 mm (0.4 to 0.9 in). Lotrich (1973, p. 381) considered this to be noteworthy because stomachs of small Kentucky arrow darters (less than 70 mm (2.8 in) TL) and stomachs of other darter species did not contain crayfishes. Other food items reported by Lotrich (1973, p. 381) and Etnier and Starnes (1993, p
8 stomachs examined by Lotrich (1973, p. 381) contained crayfishes ranging in size from 11 to 24 mm (0.4 to 0.9 in). Lotrich (1973, p. 381) considered this to be noteworthy because stomachs of small Kentucky arrow darters (less than 70 mm (2.8 in) TL) and stomachs of other darter species did not contain crayfishes. Other food items reported by Lotrich (1973, p. 381) and Etnier and Starnes (1993, p. 523) included larval blackflies (family Simuliidae) and midges (Chironomidae), with lesser amounts of caddisfly larvae, stonefly nymphs, and beetle larvae. Etnier and Starnes (1993, p. 523) reported that juvenile arrow darters feed on microcrustaceans and dipteran larvae.
Like most other darters, the Kentucky arrow darter depends on perennial stream flows that create suitable habitat conditions needed for successful completion of its life cycle. An ample supply of flowing water provides a means of transporting nutrients and food items, moderating water temperatures and dissolved oxygen levels, removing fine sediments that could damage spawning or foraging habitats, and diluting nonpoint-source pollutants. Water withdrawals do not represent a significant threat to the species, but the species is faced with occasional low-flow conditions that occur during periods of drought.
Water quality is also important to the persistence of the Kentucky arrow darter. The species requires relatively clean, cool, flowing water to successfully complete its life cycle
itats, and diluting nonpoint-source pollutants. Water withdrawals do not represent a significant threat to the species, but the species is faced with occasional low-flow conditions that occur during periods of drought.
Water quality is also important to the persistence of the Kentucky arrow darter. The species requires relatively clean, cool, flowing water to successfully complete its life cycle. Specific water quality requirements, such as temperature, dissolved oxygen, pH (a measure of the acidity or alkalinity of water), and conductivity (a measure of electrical conductance in the water column that increases as the concentration of dissolved solids
Therefore, based on the information above, we identify aquatic macroinvertebrate prey items, which are typically dominated by mayflies; permanent surface flows, as measured during average rainfall years; and adequate water quality to be physical or biological features essential to the conservaton of the Kentucky arrow darter.
Cover or Shelter
Kentucky arrow darters depend on specific habitats and bottom substrates for normal life processes such as spawning, rearing, resting, and foraging. As described above, the species typically inhabits shallow pools, riffles, runs, and glides dominated by cobble and boulder substrates and interspersed with clean sand and gravel and low levels of siltation (Thomas 2008, p. 6; Service unpublished data). Kentucky arrow darters are typically observed near some type of cover (boulders, rock ledges, large cobble, or woody debris piles) and at depths ranging from 10 to 91 cm (4 to 36 in) (Thomas 2008, p. 6; Service unpublished data). Sedimentation (siltation) has been listed repeatedly as a threat to the Kentucky arrow darter (Kuehne and Barbour 1983, p. 71; Etnier and Starnes 1993, p. 523; Thomas 2008, pp. 3-7), and the species has suffered population declines and extirpations where sedimentation has been severe (Etnier and Starnes 1993, p. 524; Thomas 2008, p. 7; Service 2012, p. 1)
mas 2008, p. 6; Service unpublished data). Sedimentation (siltation) has been listed repeatedly as a threat to the Kentucky arrow darter (Kuehne and Barbour 1983, p. 71; Etnier and Starnes 1993, p. 523; Thomas 2008, pp. 3-7), and the species has suffered population declines and extirpations where sedimentation has been severe (Etnier and Starnes 1993, p. 524; Thomas 2008, p. 7; Service 2012, p. 1). Substrates with low levels of siltation are essential in accommodating the species' feeding, breeding, growth, and other normal behaviors. The term “low levels of siltation” is defined for the purpose of this rule as silt or fine sand within interstitial spaces of substrates in amounts low enough to have minimal impact ( i.e., that would have no appreciable reduction in spawing, breeding, growth, and feeding) to the species.
Therefore, based on the information above, we identify stable, shallow pools, runs, and glides with boulder and cobble substrates, ample cover ( e.g., slab rocks, bedrock ledges, woody debris piles), to be physical or biological features essential to the conservation of the Kentucky arrow darter.
Sites for Breeding, Reproduction, or Rearing (or Development) of Offspring
Prior to spawning, male Kentucky arrow darters establish territories over riffles from March to May, when they are quite conspicuous in water 5 to 15 cm (2 to 6 in) deep (Kuehne and Barbour 1983, p. 71). Males fan out a depression in the substrate (typically a mixture of cobble, gravel, and sand) and defend these sites vigorously. Initial courtship behavior involves rapid dashes, fin-flaring, nudging, and quivering motions by the male followed by similar quivering responses of the female, who then precedes the male to the nest. The female partially buries herself in the gravel substrate, is mounted by the male, and spawning occurs (Etnier and Starnes 1993, p. 523). It is assumed that the male continues to defend the nest until the eggs have hatched
r involves rapid dashes, fin-flaring, nudging, and quivering motions by the male followed by similar quivering responses of the female, who then precedes the male to the nest. The female partially buries herself in the gravel substrate, is mounted by the male, and spawning occurs (Etnier and Starnes 1993, p. 523). It is assumed that the male continues to defend the nest until the eggs have hatched. The spawning period extends from April to June, but peak activity occurs when water temperatures reach 13 °C (55 °F), typically in mid-April (Bailey 1948, pp. 82-84; Lowe 1979, p. 44). Females produce between 200 and 600 eggs per season, with tremendous variation resulting from size, age, condition of females, and stream temperature (Rakes 2014, pers. comm.). As mentioned above, substrates with low levels of siltation are essential in accommodating the species' normal behaviors, including breeding, reproduction, and rearing. The species has suffered population declines and extirpations where sedimentation has been severe (Etnier and Starnes 1993, p. 524; Thomas 2008, p. 7; Service 2012, p. 1).
Juvenile arrow darters can exceed 25 mm (1 in) TL by mid-June and grow up to 50 mm (2 in) TL during the first year (Kuehne and Barbour 1983, p. 71; Etnier and Starnes 1993, p. 523). Juvenile arrow darters can be found throughout the channel but are often observed in shallow water along stream margins near roots mats, rock ledges, or some other cover. One-year olds are generally sexually mature and participate in spawning along with older classes (Etnier and Starnes 1993, p. 523). As stream flow lessens and riffles begin to shrink, most arrow darters move into pools and tend to remain there even when summer and autumn rains restore stream flow (Kuehne and Barbour 1983, p. 71)
ong stream margins near roots mats, rock ledges, or some other cover. One-year olds are generally sexually mature and participate in spawning along with older classes (Etnier and Starnes 1993, p. 523). As stream flow lessens and riffles begin to shrink, most arrow darters move into pools and tend to remain there even when summer and autumn rains restore stream flow (Kuehne and Barbour 1983, p. 71).
Therefore, based on the information above, we identify first- to third-order streams containing moderately flowing riffle, pool, run, and glide habitats with gravel and cobble substrates, root mats along the bank, undercut banks, and low levels of siltation to be physical or biological features essential to the conservation of the Kentucky arrow darter.
Habitats Protected From Disturbance or Representative of the Historic, Geographical, and Ecological Distributions of the Species
As described above, stable substrates with low levels of siltation, adequate water quality, and healthy aquatic insect populations are habitat features essential to the Kentucky arrow darter. Historically, first- to third-order streams across the species' range would have contained these habitat features.
All current and historical capture locations of the Kentucky arrow darter are from first- to third-order order, warmwater streams within the upper Kentucky River drainage (Gilbert 1887, pp. 53-54; Woolman 1892, pp. 275-281; Kuehne and Bailey 1961, pp. 3-4; Kuehne 1962, pp. 608-609; Thomas 2008, entire; Service 2012, entire). The species was historically distributed in at least six sub-basins of the Kentucky River, but it is now extirpated from at least 36 historical streams within those sub-basins. Forty-four percent of the species' extirpations (16 streams) have occurred since the mid-1990s, and the species appears to have disappeared completely from several minor watersheds ( e.g., Sexton Creek, South Fork Quicksand Creek, Troublesome Creek headwaters)
ted in at least six sub-basins of the Kentucky River, but it is now extirpated from at least 36 historical streams within those sub-basins. Forty-four percent of the species' extirpations (16 streams) have occurred since the mid-1990s, and the species appears to have disappeared completely from several minor watersheds ( e.g., Sexton Creek, South Fork Quicksand Creek, Troublesome Creek headwaters). Most remaining populations are highly fragmented and restricted to short stream reaches. Given the species' reduced range and fragmented distribution, it is vulnerable to extirpation from intentional or accidental toxic chemical spills, habitat modification, progressive degradation from runoff (nonpoint-source pollutants), natural catastrophic changes to their habitat ( e.g., flood scour, drought), and other stochastic disturbances, such as loss of genetic variation and inbreeding (Soulé 1980, pp. 157-158; Hunter 2002, pp. 97-101; Allendorf and Luikart 2007, pp. 117-146). In addition, the level of isolation seen in this species makes natural repopulation following localized extirpations virtually impossible without human intervention. Greater connectivity within extant populations
Based on the biological information and needs discussed above, we identify stable, undisturbed stream beds and banks, and ability for populations to be distributed in multiple first- to third-order streams throughout the upper Kentucky River drainage that are protected from disturbance or are representative of the historic, geographical, and ecological distributions of the species to be physical or biological features essential to the conservation of the Kentucky arrow darter.
Primary Constituent Elements for the Kentucky Arrow Darter
According to 50 CFR 424.12(b), we are required to identify the physical or biological features essential to the conservation of the Kentucky arrow darter in areas occupied at the time of listing, focusing on the features' primary constituent elements
cal or biological features essential to the conservation of the Kentucky arrow darter.
Primary Constituent Elements for the Kentucky Arrow Darter
According to 50 CFR 424.12(b), we are required to identify the physical or biological features essential to the conservation of the Kentucky arrow darter in areas occupied at the time of listing, focusing on the features' primary constituent elements. We consider primary constituent elements to be those specific elements of the physical or biological features that provide for a species' life-history processes and are essential to the conservation of the species.
Based on our current knowledge of the physical or biological features and habitat characteristics required to sustain the species' life-history processes, we determine that the primary constituent elements specific to the Kentucky arrow darter are:
(1) Primary Constituent Element 1—Riffle-pool complexes and transitional areas (glides and runs) of geomorphically stable, first- to third-order streams with connectivity between spawning, foraging, and resting sites to promote gene flow throughout the species' range.
(2) Primary Constituent Element 2—Stable bottom substrates composed of gravel, cobble, boulders, bedrock ledges, and woody debris piles with low levels of siltation.
(3) Primary Constituent Element 3—An instream flow regime (magnitude, frequency, duration, and seasonality of discharge over time) sufficient to provide permanent surface flows, as measured during years with average rainfall, and to maintain benthic habitats utilized by the species.
(4) Primary Constituent Element 4—Adequate water quality characterized by moderate stream temperatures, acceptable dissolved oxygen concentrations, moderate pH, and low levels of pollutants. Adequate water quality is defined for the purpose of this rule as the quality necessary for normal behavior, growth, and viability of all life stages of the Kentucky arrow darter.
s utilized by the species.
(4) Primary Constituent Element 4—Adequate water quality characterized by moderate stream temperatures, acceptable dissolved oxygen concentrations, moderate pH, and low levels of pollutants. Adequate water quality is defined for the purpose of this rule as the quality necessary for normal behavior, growth, and viability of all life stages of the Kentucky arrow darter.
(5) Primary Constituent Element 5—A prey base of aquatic macroinvertebrates, including mayfly nymphs, midge larvae, caddisfly larvae, stonefly nymphs, and small crayfishes.
Special Management Considerations or Protection
When designating critical habitat, we assess whether the specific areas within the geographical area occupied by the species at the time of listing contain features which are essential to the conservation of the species and which may require special management considerations or protection. The 38 units we are proposing to designate as critical habitat for the Kentucky arrow darter will require some level of management to address the current and future threats to the physical or biological features of the species. Due to their location on the Daniel Boone National Forest (DBNF), at least a portion of 20 proposed critical habitat units (Units 15-16, 18-32, and 36-38) are being managed and protected under DBNF's land and resource management plan (LRMP) (United States Forest Service (USFS) 2004, pp. 1-14), and additional conservation measures will be provided upon completion of a candidate conservation agreement between DBNF and the Service (see Available Conservation Measures section of the proposed listing rule published elsewhere in today's Federal Register )
are being managed and protected under DBNF's land and resource management plan (LRMP) (United States Forest Service (USFS) 2004, pp. 1-14), and additional conservation measures will be provided upon completion of a candidate conservation agreement between DBNF and the Service (see Available Conservation Measures section of the proposed listing rule published elsewhere in today's Federal Register ).
Two of the 38 proposed critical habitat units (Units 3 and 4) are located wholly (Unit 3) or partially (Unit 4) on State property, specifically Robinson Forest, a 4,047-hectare (10,000-acre) research, education, and extension forest in Breathitt and Knott Counties owned by the University of Kentucky (UK) and managed by the Department of Forestry in the College of Agriculture, Food, and Environment. Management guidelines approved by the University of Kentucky's Board of Trustees in 2004 provide general land use allocations, sustainable allowances for active research and demonstration projects involving overstory manipulation, allocations of net revenues from research and demonstration activities, and management and oversight responsibilities (Stringer 2015, pers. comm.). Activities within Robinson Forest may require special management considerations or protection to address minor siltation associated with timber management research, stormwater runoff from unpaved roads, and limited off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
At least portions of 32 proposed critical habitat units are located on private property (16 are located entirely on private property) and are not presently under the protection provided by the management plan or candidate conservation agreement for the species. Activities in or adjacent to these areas of proposed critical habitat may affect one or more of the physical or biological features essential to the Kentucky arrow darter
critical habitat units are located on private property (16 are located entirely on private property) and are not presently under the protection provided by the management plan or candidate conservation agreement for the species. Activities in or adjacent to these areas of proposed critical habitat may affect one or more of the physical or biological features essential to the Kentucky arrow darter. For example, features in this proposed critical habitat designation may require special management due to threats associated with resource extraction (coal surface mining, logging, natural gas and oil exploration), agricultural runoff (livestock, row crops), lack of adequate riparian buffers, construction and maintenance of State and county roads, land development, off-road vehicle use, and other nonpoint-source pollution. These threats are in addition to adverse effects of drought, floods, or other natural phenomena. Other activities that may affect physical and biological features in the proposed critical habitat units include those listed in the Effects of Critical Habitat Designation section, below.
Management activities that could ameliorate these threats include, but are not limited to, the use of best management practices (BMPs) designed to reduce sedimentation, erosion, and stream bank destruction; development of alternatives that avoid and minimize stream bed disturbances; an increase of stormwater management and reduction of stormwater flows into stream systems; preservation of headwater springs and streams; regulation of off-road vehicle use; and reduction of other watershed and floodplain disturbances that release sediments, pollutants, or nutrients into the water.
In summary, we find that the areas we are proposing as critical habitat for the Kentucky arrow darter that are occupied at the time of listing contain the physical or biological features for the species, and that these features may require special management considerations or protection
f other watershed and floodplain disturbances that release sediments, pollutants, or nutrients into the water.
In summary, we find that the areas we are proposing as critical habitat for the Kentucky arrow darter that are occupied at the time of listing contain the physical or biological features for the species, and that these features may require special management considerations or protection. Special management consideration or protection may be required to eliminate, or to reduce to negligible levels, the threats affecting the physical or biological features of each unit. Additional discussion of threats facing individual units is provided in the individual unit descriptions below.
Criteria Used To Identify Critical Habitat
As required by section 4(b)(2) of the Act, we use the best scientific data available to designate critical habitat. In accordance with the Act and our implementing regulations at 50 CFR 424.12(b) we review available information pertaining to the habitat requirements of the species and identify occupied areas at the time of listing that contain the features essential to the conservation of the species. If after identifying occupied areas, a determination is made that those areas are inadequate to ensure conservation of the species, in accordance with the Act and our implementing regulations at 50 CFR 424.12(e), we then consider whether designating additional areas—outside those occupied at the time of listing—are essential for the conservation of the species. We are not currently proposing to designate any areas outside the geographical area occupied by the species because we believe that occupied areas (a total of 47 streams) are adequate to ensure the conservation of the species. The following discussion describes how we identified and delineated those occupied areas.
We began our analysis by considering the historical and current ranges of the Kentucky arrow darter
ly proposing to designate any areas outside the geographical area occupied by the species because we believe that occupied areas (a total of 47 streams) are adequate to ensure the conservation of the species. The following discussion describes how we identified and delineated those occupied areas.
We began our analysis by considering the historical and current ranges of the Kentucky arrow darter. We used various sources including published literature, museum collection databases, surveys, reports, and collection records obtained from the KDFWR, Kentucky State Nature Preserves Commission, Kentucky Division of Water, and our own files (see “Historical Range and Distribution” and “Current Range and Distribution” sections of our proposed listing rule published elsewhere in today's Federal Register ). We then identified the specific areas that are occupied by the species and that contain one or more of the physical or biological features essential to the species' conservation. We defined occupied habitat as those stream reaches known to be currently occupied by the species. To identify the currently occupied stream reaches, we used post-2006 survey data that provided information on distribution and habitat condition (Thomas 2008, entire; Service 2012, entire; Service unpublished data). Generally, if the species was collected or observed in a particular stream during our recent rangewide surveys (2007-2014), the stream reach was considered to be occupied. A few transient individuals were observed in streams with unsuitable habitat conditions ( e.g., elevated conductivity), but these streams were not considered to be occupied due to the poor habitat conditions and the high likelihood that these individuals had simply migrated from a nearby source stream. To identify the unoccupied stream reaches, we evaluated historical data (late 1880s-2006) and the results of our recent surveys (2007-2014) (Thomas 2008, entire; Service 2012, entire; Service unpublished data)
vity), but these streams were not considered to be occupied due to the poor habitat conditions and the high likelihood that these individuals had simply migrated from a nearby source stream. To identify the unoccupied stream reaches, we evaluated historical data (late 1880s-2006) and the results of our recent surveys (2007-2014) (Thomas 2008, entire; Service 2012, entire; Service unpublished data). If the species was known to occur in a stream prior to 2007, but was not observed during our recent rangewide survey, the stream reach was considered to be unoccupied.
Based on our review, we made a determination to not propose to designate as critical habitat any unoccupied stream reaches. We concluded that the proposed units occupied by the species at the time of listing are representative of the species' historical range and include both the core population areas of Kentucky arrow darters, as well as remaining peripheral population areas. We determined that there was sufficient area for the conservation of the species within the occupied areas.
Following the identification of occupied stream reaches, the next step was to delineate the probable upstream and downstream extent of the species' distribution. We used U.S. Geological Survey (USGS) 1:100,000 digital stream maps to delineate these boundaries of proposed critical habitat units according to the criteria explained below. We set the upstream and downstream limits of each critical habitat unit by identifying landmarks (bridges, confluences, and road crossings), and in some instances latitude and longitude coordinates and secton lines, above and below the upper and lowermost reported locations of the Kentucky arrow darter in each stream reach to ensure incorporation of all potential sites of occurrence. We considered stream order and watershed size to select the upstream terminus
at unit by identifying landmarks (bridges, confluences, and road crossings), and in some instances latitude and longitude coordinates and secton lines, above and below the upper and lowermost reported locations of the Kentucky arrow darter in each stream reach to ensure incorporation of all potential sites of occurrence. We considered stream order and watershed size to select the upstream terminus. The species can occur in small, first-order reaches (Thomas 2008, entire; Service 2012, entire), but recent surveys have also demonstrated that the species is typically absent in these reaches once the watershed size (the upstream basin or catchment) falls below 1.3 square kilometers (km 2 ) (0.5 square miles (mi 2 )). Consequently, we searched for this point within the watershed and selected the nearest tributary confluence as the upstream terminus. When a tributary was not available, a road-crossing (bridge or ford) or dam was used to mark the boundary. For the downstream boundary of a unit, we typically selected a stream confluence of a named tributary below the downstream-most occurrence record and within a third-order or smaller stream reach. In the unit descriptions, distances between landmarks used to identify the upstream or downstream extent of a stream segment are given in stream kilometers and equivalent miles, as measured tracing the course of the stream, not straight-line distance. The proposed critical habitat areas were then mapped using ArcGIS software to produce the critical habitat unit maps.
Because fishes are naturally restricted by certain physical conditions within a stream reach ( i.e., flow, substrate, cover), they may be unevenly distributed within these habitat units. Uncertainty on some downstream distributional limits for some populations ( e.g., Frozen Creek) may have resulted in small areas of occupied habitat not being included in, or areas of unoccupied habitat included in, the designation
naturally restricted by certain physical conditions within a stream reach ( i.e., flow, substrate, cover), they may be unevenly distributed within these habitat units. Uncertainty on some downstream distributional limits for some populations ( e.g., Frozen Creek) may have resulted in small areas of occupied habitat not being included in, or areas of unoccupied habitat included in, the designation. We recognize that both historical and recent collection records upon which we relied are incomplete, and that there may be stream segments or small tributaries not included in this proposed designation that harbor small, limited populations of the species considered in this proposed designation, or that others may become suitable in the future. The omission of such areas does not diminish their potential individual or cumulative importance to the conservation of the Kentucky arrow darter. The habitat areas contained within the proposed units described below constitute our best evaluation of areas needed for the conservation of this species at this time.
The areas proposed for critical habitat below include only stream channels within the ordinary high-water line and do not contain any developed areas or structures. When determining proposed critical habitat boundaries, we made every effort to avoid including developed areas such as lands covered by buildings, pavement, and other structures because such areas usually lack physical and biological features essential to the conservation of the species. The scale of the maps we prepared under the parameters for publication within the Code of Federal Regulations may not reflect the exclusion of such developed areas. Any such areas inadvertently left inside critical habitat boundaries shown on the maps of this proposed rule have been excluded by text in the proposed rule and are not proposed for designation as critical habitat
ation of the species. The scale of the maps we prepared under the parameters for publication within the Code of Federal Regulations may not reflect the exclusion of such developed areas. Any such areas inadvertently left inside critical habitat boundaries shown on the maps of this proposed rule have been excluded by text in the proposed rule and are not proposed for designation as critical habitat. Therefore, if the critical habitat is finalized as proposed, a Federal action involving these areas would not trigger section 7 consultation with respect to critical habitat and the requirement of no adverse modification unless the specific action would affect the physical or biological features in the
The proposed critical habitat designation is defined by the map or maps, as modified by any accompanying regulatory text, presented at the end of this document in the Proposed Regulation Promulgation section. We include more detailed information on the boundaries of the proposed critical habitat designation in the individual unit descriptions below. We will make the coordinates, plot points, or both on which each map is based available to the public on http://www.regulations.gov at Docket No. FWS-R4-ES-2015-0133, on our Internet site at http://www.fws.gov/frankfort/ , and at the field office responsible for the designation (see FOR FURTHER INFORMATION CONTACT , above).
Proposed Critical Habitat Designation
We are proposing to designate approximately 395 skm (246 smi) in 38 units as critical habitat in Kentucky for the Kentucky arrow darter. These stream reaches comprise the entire currently known range of the species (and all extant populations). All proposed units are considered to be occupied at the time of listing and contain the physical or biological features in the appropriate quantity and spatial arrangement essential to the conservation of this species and support multiple life-history processes for the Kentucky arrow darter. The 38 areas we propose as critical habitat are listed in Table 1 below
ecies (and all extant populations). All proposed units are considered to be occupied at the time of listing and contain the physical or biological features in the appropriate quantity and spatial arrangement essential to the conservation of this species and support multiple life-history processes for the Kentucky arrow darter. The 38 areas we propose as critical habitat are listed in Table 1 below.
Critical habitat units are either in private, Federal (DBNF), or State (UK) ownership. In Kentucky, adjacent landowners also own the land under streams ( e.g., the stream channel or bottom), but the water is under State jurisdiction. Portions of the public-to-private boundary for Units 16, 18, 19, 21, 22, 24, 32, and 36 were located along the mid-line of the stream channel; lengths for these segments were divided equally between public and private ownership. Ownership and lengths of proposed Kentucky arrow darter critical habitat units are provided in Table 1.
Table 1—Location, Ownership, and Lengths for Proposed Kentucky Arrow Darter Critical Habitat Units Unit Stream County Ownership—skm (smi) Private Federal State Total length skm (smi) 1 Buckhorn Creek and Prince Fork Knott 1.1 (0.7) 0 0 1.1 (0.7) 2 Eli Fork Knott 1.0 (0.6) 0 0 1.0 (0.6) 3 Coles Fork and Snag Ridge Fork Breathitt, Knott 0 0 11.0 (6.8) 11.0 (6.8) 4 Clemons Fork Breathitt 0.1 (0.1) 0 6.9 (4.3) 7.0 (4.4) 5 Laurel Fork Quicksand Creek and Tributaries Knott 19.8 (12.4) 0 0 19.8 (12.4) 6 Middle Fork Quicksand Creek and Tributaries Knott 22.5 (13.9) 0 0 22.5 (13.9) 7 Spring Fork Quicksand Creek Breathitt 2.2 (1.4) 0 0 2.2 (1.4) 8 Hunting Creek and Tributaries Breathitt 15.6 (9.7) 0 0 15.6 (9.7) 9 Frozen Creek and Tributaries Breathitt 26.4 (16.4) 0 0 26.4 (16.4) 10 Holly Creek and Tributaries Wolfe 18.3 (11.5) 0 0 18.3 (11.5) 11 Little Fork Lee, Wolfe 3.8 (2.3) 0 0 3.8 (2.3) 12 Walker Creek and Tributaries Lee, Wolfe 25.0 (15.5) 0 0 25.0 (15.5) 13 Hell Creek and Tributaries Lee 12.0 (7.4) 0 0 12.0 (7.4) 14 Big Laurel Creek Harlan 9.1 (5.7) 0 0 9.1 (5.
Breathitt 15.6 (9.7) 0 0 15.6 (9.7) 9 Frozen Creek and Tributaries Breathitt 26.4 (16.4) 0 0 26.4 (16.4) 10 Holly Creek and Tributaries Wolfe 18.3 (11.5) 0 0 18.3 (11.5) 11 Little Fork Lee, Wolfe 3.8 (2.3) 0 0 3.8 (2.3) 12 Walker Creek and Tributaries Lee, Wolfe 25.0 (15.5) 0 0 25.0 (15.5) 13 Hell Creek and Tributaries Lee 12.0 (7.4) 0 0 12.0 (7.4) 14 Big Laurel Creek Harlan 9.1 (5.7) 0 0 9.1 (5.7) 15 Laurel Creek Leslie 0.7 (0.5) 3.4 (2.1) 0 4.1 (2.6) 16 Hell For Certain Creek and Tributaries Leslie 11.4 (7.0) 4.4 (2.8) 0 15.8 (9.8) 17 Squabble Creek Perry 12.0 (7.5) 0 0 12.0 (7.5) 18 Blue Hole Creek and Left Fork Blue Hole Creek Clay 0 5.7 (3.5) 0 5.7 (3.5) 19 Upper Bear Creek and Tributaries Clay 0.2 (0.1) 6.6 (4.2) 0 6.8 (4.3) 20 Katies Creek Clay 1.7 (1.0) 4.0 (2.5) 0 5.7 (3.5) 21 Spring Creek and Little Spring Creek Clay 3.6 (2.2) 5.6 (3.5) 0 9.2 (5.7) 22 Bowen Creek and Tributaries Leslie 2.0 (1.2) 11.6 (7.3) 0 13.6 (8.5) 23 Elisha Creek and Tributaries Leslie 3.0 (1.9) 6.6 (4.0) 0 9.6 (5.9) 24 Gilberts Big Creek Clay, Leslie 2.0 (1.2) 5.2 (3.3) 0 7.2 (4.5) 25 Sugar Creek Clay, Leslie 1.1 (0.7) 6.1 (3.8) 0 7.2 (4.5) 26 Big Double Creek and Tributaries Clay 0 10.3 (6.4) 0 10.3 (6.4) 27 Little Double Creek Clay 0 3.4 (2.1) 0 3.4 (2.1) 28 Jacks Creek Clay 5.4 (3.4) 0.5 (0.3) 0 5.9 (3.7) 29 Long Fork Clay 0 2.2 (1.4) 0 2.2 (1.4) 30 Horse Creek Clay 3.0 (1.9) 2.0 (1.2) 0 5.0 (3.1) 31 Bullskin Creek Clay, Leslie 21.3 (13.3) 0.4 (0.2) 0 21.7 (13.5) 32 Buffalo Creek and Tributaries Owsley 23.2 (14.5) 14.9 (9.3) 0 38.1 (23.8) 33 Lower Buffalo Creek Lee, Owsley 7.3 (4.6) 0 0 7.3 (4.6) 34 Silver Creek Lee 6.2 (3.9) 0 0 6.2 (3.9) 35 Travis Creek Jackson 4.1 (2.5) 0 0 4.1 (2.5) 36 Wild Dog Creek Jackson, Owsley 4.3 (2.7) 3.8 (2.4) 0 8.1 (5.1) 37 Granny Dismal Creek Lee, Owsley 4.4 (2.7) 2.5 (1.6) 0 6.9 (4.3) 38 Rockbridge Fork Wolfe 0 4.5 (2.8) 0 4.5 (2.8) Total 273.8 (170.3) 103.7 (64.7) 17.9 (11.1) 395.4 (246.1) We present brief descriptions of all units below
4.6) 0 0 7.3 (4.6) 34 Silver Creek Lee 6.2 (3.9) 0 0 6.2 (3.9) 35 Travis Creek Jackson 4.1 (2.5) 0 0 4.1 (2.5) 36 Wild Dog Creek Jackson, Owsley 4.3 (2.7) 3.8 (2.4) 0 8.1 (5.1) 37 Granny Dismal Creek Lee, Owsley 4.4 (2.7) 2.5 (1.6) 0 6.9 (4.3) 38 Rockbridge Fork Wolfe 0 4.5 (2.8) 0 4.5 (2.8) Total 273.8 (170.3) 103.7 (64.7) 17.9 (11.1) 395.4 (246.1) We present brief descriptions of all units below. We consider each proposed unit to contain all the physical or biological features and primary constituent elements (PCEs) identified above that are essential to the conservation of the species. In general, stream channels within these units are stable, with ample pool, glide, riffle, and run habitats (PCE 1) that maintain surface flows year round (PCE 3) and contain gravel, cobble, and boulder substrates with low levels of siltation (PCE 2). Such characteristics are necessary for reproductive, foraging, and sheltering requirements of Kentucky arrow darters. We consider water quality in each of these units to be characterized by moderate temperatures, relatively high dissolved oxygen concentrations, moderate pH, and low levels of pollutants (PCE 4). These conditions support abundant populations of aquatic macro­inverte­brates that serve as prey items for Kentucky arrow darters (PCE 5).
The proposed critical habitat units include the stream channels of the creek within the ordinary high water line. As defined at 33 CFR 329.11, the ordinary high water mark on nontidal rivers is the line on the shore established by the fluctuations of water and indicated by physical characteristics, such as a clear, natural line impressed on the bank; shelving; changes in the character of soil; destruction of terrestrial vegetation; the presence of litter and debris; or other appropriate means that consider the characteristics of the surrounding areas. For each stream reach proposed as a critical habitat unit, the upstream and downstream boundaries are described generally below
aracteristics, such as a clear, natural line impressed on the bank; shelving; changes in the character of soil; destruction of terrestrial vegetation; the presence of litter and debris; or other appropriate means that consider the characteristics of the surrounding areas. For each stream reach proposed as a critical habitat unit, the upstream and downstream boundaries are described generally below. More precise definitions are provided in the Proposed Regulation Promulgation at the end of this proposed rule.
Unit 1: Buckhorn Creek and Prince Fork, Knott County, Kentucky
Proposed Unit 1 is located off Buckhorn Road in the headwaters of the Buckhorn Creek drainage and between Kentucky Highway 1098 (KY 1098) and KY 1087. It includes 0.7 skm (0.4 smi) of Prince Fork from its confluence with Mart Branch downstream to its confluence with Buckhorn Creek and 0.4 skm (0.3 smi) of Buckhorn Creek from its confluence with Prince Fork downstream to its confluence with Emory Branch. Live Kentucky arrow darters have been collected from proposed Unit 1 in Prince Fork and just upstream of the confluence of Buckhorn Creek and Emory Branch (ATS 2011, p. 6; Service 2012, pp. 1-4). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. The watershed surrounding proposed Unit 1 is dominated by forest and remains relatively undisturbed; however, downstream reaches of Buckhorn Creek have been degraded by siltation and nonpoint-source pollutants associated with surface coal mining, oil and gas exploration, logging, and runoff from unpaved roads (Service 2012, pp. 1-4). This unit helps to maintain the geographical range of the species (adds population redundancy) and provides opportunity for population growth
relatively undisturbed; however, downstream reaches of Buckhorn Creek have been degraded by siltation and nonpoint-source pollutants associated with surface coal mining, oil and gas exploration, logging, and runoff from unpaved roads (Service 2012, pp. 1-4). This unit helps to maintain the geographical range of the species (adds population redundancy) and provides opportunity for population growth.
Within proposed Unit 1, the Kentucky arrow darter and its habitat may require special management considerations or protection to address potential adverse effects ( e.g., water pollution, siltation) associated with surface coal mining, logging (timber harvests on private land), natural gas and oil exploration, construction and maintenance of county roads (Buckhorn Road), the lack of adequate riparian buffers (near the confluence with Emory Branch), and off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 2: Eli Fork, Knott County, Kentucky
This proposed unit is located in the headwaters of the Buckhorn Creek drainage between KY 1098 and KY 1087. It includes 1.0 skm (0.6 smi) of Eli Fork from its confluence with Stonecoal Branch downstream to its confluence with Boughcamp Branch (of Buckhorn Creek). Live Kentucky arrow darters have been collected from proposed Unit 2 near the confluence of Eli Fork and Boughcamp Branch (ATS 2011, p. 6). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. The watershed surrounding proposed Unit 2 is dominated by forest and remains relatively undisturbed; however, its receiving stream, Boughcamp Branch, and adjacent watersheds have been degraded by siltation and nonpoint-source pollutants associated with surface coal mining and logging (Service 2012, pp. 1-4). This unit helps to maintain the geographical range of the species (adds population redundancy) and provides opportunity for population growth
ted by forest and remains relatively undisturbed; however, its receiving stream, Boughcamp Branch, and adjacent watersheds have been degraded by siltation and nonpoint-source pollutants associated with surface coal mining and logging (Service 2012, pp. 1-4). This unit helps to maintain the geographical range of the species (adds population redundancy) and provides opportunity for population growth.
Within proposed Unit 2, the Kentucky arrow darter and its habitat may require special management considerations or protection to address potential adverse effects ( e.g., water pollution, siltation) associated with surface coal mining, logging, natural gas and oil exploration, off-road vehicle use, and construction and maintenance of county roads. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 3: Coles Fork and Snag Ridge Fork, Breathitt and Knott Counties, Kentucky
This proposed unit is located entirely within Robinson Forest, a 4,047-hectare (10,000-acre) research, education, and extension forest in Breathitt and Knott Counties owned by UK and managed by the Department of Forestry in the College of Agriculture, Food, and Environment. Unit 3 includes 2.1 skm (1.3 smi) of Snag Ridge Fork from its headwaters downstream to its confluence with Coles Fork and 8.9 skm (5.5 smi) of Coles Fork from its confluence with Saddle Branch downstream to its confluence with Buckhorn Creek. Live Kentucky arrow darters have been observed throughout proposed Unit 3 (Thomas 2008, p. 5; Service 2012, pp. 1-4), and Coles Fork continues to be one of the species' best remaining habitats. This unit is located entirely on lands owned by UK. The watershed surrounding proposed Unit 3 is intact and densely forested, water quality conditions are excellent (very close to baseline levels), and instream habitats are ideal for the species. This unit represents a stronghold for the species (core population) and likely contributes to range expansion (source population)
est remaining habitats. This unit is located entirely on lands owned by UK. The watershed surrounding proposed Unit 3 is intact and densely forested, water quality conditions are excellent (very close to baseline levels), and instream habitats are ideal for the species. This unit represents a stronghold for the species (core population) and likely contributes to range expansion (source population).
Within proposed Unit 3, the Kentucky arrow darter and its habitat may require special management considerations or protection to address siltation associated with timber management (on Robinson Forest), stormwater runoff from unpaved roads, and limited off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 4: Clemons Fork, Breathitt County, Kentucky
Proposed Unit 4 is located along Clemons Fork Road in southeastern Breathitt County. This unit includes 7.0 skm (4.4 smi) of Clemons Fork from its confluence with Maple Hollow downstream to its confluence with Buckhorn Creek. Live Kentucky arrow darters have been observed throughout proposed Unit 4 (Lotrich 1973, p. 380; Thomas 2008, p. 5; Service 2012, pp. 1-4). A portion of this unit near the mouth of Clemons Fork is privately owned (0.1 skm (0.1 smi)), but the majority is located on lands owned by UK (see description for Unit 3). The watershed surrounding proposed Unit 4 is intact and densely forested, water quality conditions are excellent (very close to baseline levels), and instream habitats
Within proposed Unit 4, the Kentucky arrow darter and its habitat may require special management considerations or protection to address siltation associated with timber management (on Robinson Forest), stormwater runoff from unpaved roads, and limited off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena
vels), and instream habitats
Within proposed Unit 4, the Kentucky arrow darter and its habitat may require special management considerations or protection to address siltation associated with timber management (on Robinson Forest), stormwater runoff from unpaved roads, and limited off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 5: Laurel Fork Quicksand Creek and Tributaries, Knott County, Kentucky
Proposed Unit 5 generally runs parallel to KY 1098 and Laurel Fork Road in northern Knott County. This unit includes 1.2 skm (0.8 smi) of Fitch Branch from its headwaters downstream to its confluence with Laurel Fork Quicksand Creek, 2.7 skm (1.7 smi) of Newman Branch from its headwaters downstream to its confluence with Laurel Fork Quicksand Creek, 2.1 skm (1.3 smi) of Combs Branch from its headwaters downstream to its confluence with Laurel Fork Quicksand Creek, and 13.8 skm (8.6 smi) of Laurel Fork Quicksand Creek from KY 80 downstream to its confluence with Patten Fork. Live Kentucky arrow darters have been captured within proposed Unit 5 just upstream of the Laurel Fork and Patten Fork confluence and farther upstream at the first Laurel Fork Road crossing (Thomas 2008, p. 5; Service 2012, pp. 1-4). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. Hillsides and ridgetops above proposed Unit 5 are forested, but the valley is more developed with scattered residences along Laurel Fork Road. This unit helps to maintain the geographical range of the species (adds population redundancy) and likely serves as a source population within the Quicksand Creek watershed
ll amount that is publicly owned in the form of bridge crossings and road easements. Hillsides and ridgetops above proposed Unit 5 are forested, but the valley is more developed with scattered residences along Laurel Fork Road. This unit helps to maintain the geographical range of the species (adds population redundancy) and likely serves as a source population within the Quicksand Creek watershed.
Within proposed Unit 5, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with logging, inadequate sewage treatment, surface coal mining, natural gas and oil exploration activities, inadequate riparian buffers, construction and maintenance of county roads, and off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 6: Middle Fork Quicksand Creek and Tributaries, Knott County, Kentucky
Proposed Unit 6 is located along Middle Fork of Quicksand Creek Road in northeastern Knott County. This unit includes 0.8 skm (0.5 smi) of Big Firecoal Branch from its headwaters downstream to its confluence with Middle Fork Quicksand Creek, 2.1 skm (1.3 smi) of Bradley Branch from its headwaters downstream to its confluence with Middle Fork Quicksand Creek, 2.0 skm (1.2 smi) of Lynn Log Branch from its headwaters downstream to its confluence with Middle Fork Quicksand Creek, and 17.6 skm (10.9 smi) of Middle Fork Quicksand Creek from its headwaters downstream to its confluence with Big Branch. Live Kentucky arrow darters have been captured within proposed Unit 6 near the confluence of Middle Fork and Jack Branch and the confluence of Middle Fork and Upper Bear Pen Branch (Thomas 2008, p. 5; Service 2012, pp. 1-4). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements
ce with Big Branch. Live Kentucky arrow darters have been captured within proposed Unit 6 near the confluence of Middle Fork and Jack Branch and the confluence of Middle Fork and Upper Bear Pen Branch (Thomas 2008, p. 5; Service 2012, pp. 1-4). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. The watershed surrounding proposed Unit 6 is dominated by forest and continues to be relatively undisturbed. An unpaved, road traverses the length of the unit, but the rough condition of the road limits its use to off-road vehicles. This unit helps to maintain the geographical range of the species (adds population redundancy) and likely serves as a source population within the Quicksand Creek watershed.
Within proposed Unit 6, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with natural gas and oil exploration activities, logging, surface coal mining, inadequate riparian buffers, construction and maintenance of county roads, and off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 7: Spring Fork Quicksand Creek, Breathitt County, Kentucky
Proposed Unit 7 is located of KY 2465 in southeastern Breathitt County and includes 2.2 skm (1.4 smi) of Spring Fork Quicksand Creek from its headwaters downstream to its confluence with an unnamed tributary. Live Kentucky arrow darters have been captured within proposed Unit 7 (Service unpublished data). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. Most of the watershed surrounding proposed Unit 7 is forested, but mine reclamation activities have created open, pasture-like habitats along ridgetops and slopes to the north
ve been captured within proposed Unit 7 (Service unpublished data). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. Most of the watershed surrounding proposed Unit 7 is forested, but mine reclamation activities have created open, pasture-like habitats along ridgetops and slopes to the north. This unit helps to maintain the geographical range of the species within the Quicksand Creek watershed (adds population redundancy) and provides opportunity for population growth.
Within proposed Unit 7, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with surface coal mining, natural gas and oil exploration activities, logging, and off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 8: Hunting Creek and Tributaries, Breathitt County, Kentucky
Proposed Unit 8 is located along KY 1094 in eastern Breathitt County and includes 0.9 skm (0.5 smi) of Wolf Pen Branch from its headwaters downstream to its confluence with Hunting Creek, 2.3 skm (1.4 smi) of Fletcher Fork from its headwaters downstream to its confluence with Hunting Creek, 1.6 skm (1.0 smi) of Negro Fork from its headwaters downstream to its confluence with Hunting Creek, 3.1 skm (1.9 smi) of Licking Fork from its headwaters downstream to its confluence with Hunting Creek, and 7.7 skm (4.8 smi) of Hunting Creek from its confluence with Wells Fork downstream to its confluence with Quicksand Creek. Live Kentucky arrow darters have been captured within proposed Unit 8 near the confluence with Winnie Branch (Service unpublished data). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements
mi) of Hunting Creek from its confluence with Wells Fork downstream to its confluence with Quicksand Creek. Live Kentucky arrow darters have been captured within proposed Unit 8 near the confluence with Winnie Branch (Service unpublished data). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. The narrow valley surrounding proposed Unit 8 contains a few scattered residences and fields along Hunting Creek Road, but the majority of the watershed is relatively intact and dominated by forest. This unit helps to maintain the geographical range of the species within the Quicksand Creek watershed (adds population redundancy) and provides opportunity for population growth.
Within proposed Unit 8, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with natural gas and oil exploration activities, logging, surface
Unit 9: Frozen Creek and Tributaries, Breathitt County, Kentucky
Proposed Unit 9 is located along KY 378 in northern Breathitt County. This unit includes 4.7 skm (2.9 smi) of Clear Fork from its headwaters downstream to its confluence with Frozen Creek, 3.6 skm (2.3 smi) of Negro Branch from its headwaters downstream to its confluence with Frozen Creek, 4.2 skm (2.6 smi) of Davis Creek from its headwaters downstream to its confluence with Frozen Creek, and 13.9 skm (8.6 smi) of Frozen Creek from its headwaters downstream to its confluence with Morgue Fork. Live Kentucky arrow darters have been captured within proposed Unit 9 upstream of Rock Lick in the headwaters of Frozen Creek (Thomas 2008, p. 5; Service unpublished data). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements
reek from its headwaters downstream to its confluence with Morgue Fork. Live Kentucky arrow darters have been captured within proposed Unit 9 upstream of Rock Lick in the headwaters of Frozen Creek (Thomas 2008, p. 5; Service unpublished data). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. The individual valleys surrounding proposed Unit 9 are relatively narrow (approximately 100-160 meters (m) (328-525 feet (ft)) at their widest) and comprised of small farms and scattered residences. The ridgetops and hillsides are relatively undisturbed and dominated by forest. This unit helps to maintain the geographical range of the species (adds population redundancy), contributes to genetic exchange between several streams in the Frozen Creek watershed, and likely serves as an important source population in the northern limits of the species' range.
Within proposed Unit 9, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with inadequate sewage treatment, canopy loss, agricultural runoff, inadequate riparian buffers, construction and maintenance of county roads, logging, natural gas and oil exploration activities, surface coal mining (legacy effects), and off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena
e.g., siltation, water pollution) associated with inadequate sewage treatment, canopy loss, agricultural runoff, inadequate riparian buffers, construction and maintenance of county roads, logging, natural gas and oil exploration activities, surface coal mining (legacy effects), and off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 10: Holly Creek and Tributaries, Wolfe County, Kentucky
Proposed Unit 10 is located along KY 1261 in southern Wolfe County and includes 2.8 skm (1.8 smi) of Spring Branch from its headwaters downstream to its confluence with Holly Creek, 2.0 skm (1.3 smi) of Pence Branch from its headwaters downstream to its confluence with Holly Creek, 4.0 skm (2.5 smi) of Cave Branch from its headwaters downstream to its confluence with Holly Creek, and 9.5 skm (5.9 smi) of Holly Creek from KY 1261 (first bridge crossing north of KY 15) downstream to its confluence with the North Fork Kentucky River. Live Kentucky arrow darters have been captured within proposed Unit 10 near the confluence of Holly Creek and Spring Branch (Thomas 2008, p. 5). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. This unit helps to maintain the geographical range of the species and provides opportunity for population growth.
The valley bottom surrounding proposed Unit 10 is consistently wider (approximately 320 m (1050 ft) at its widest) than other occupied stream valleys ( e.g., Frozen Creek), and agricultural land use is more extensive. Multiple small farms ( e.g., pasture, row crops, hayfields) and residences are scattered along KY 1261, while the ridgetops and hillsides are dominated by forest. We are not designating critical habitat in upstream reaches of the drainage ( e.g., Kelse Holland Fork, Mandy Holland Fork, Terrell Fork) because these streams do not contain the PCEs essential to the species' conservation
ore extensive. Multiple small farms ( e.g., pasture, row crops, hayfields) and residences are scattered along KY 1261, while the ridgetops and hillsides are dominated by forest. We are not designating critical habitat in upstream reaches of the drainage ( e.g., Kelse Holland Fork, Mandy Holland Fork, Terrell Fork) because these streams do not contain the PCEs essential to the species' conservation. Habitat conditions in these upstream reaches are poor, as characterized by straightened, incised channels; a lack of canopy cover; and unstable substrates.
Within proposed Unit 10, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with agricultural runoff, canopy loss, inadequate riparian buffers, construction and maintenance of county roads, inadequate sewage treatment, logging, surface coal mining (legacy effects), and off-road vehicle use. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 11: Little Fork, Lee and Wolfe County, Kentucky
This proposed unit is located between KY 2016 and Booth Ridge Road in southern Wolfe County and includes 3.8 skm (2.3 smi) of Little Fork from its headwaters downstream to its confluence with Lower Devil Creek. Live Kentucky arrow darters have been captured within proposed Unit 11 just upstream of the confluence of Little Fork and Lower Devil Creek (Thomas 2008, p. 5; Service 2012, pp. 1-4). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. This unit helps to maintain the geographical range of the species (population redundancy) and provides opportunity for population growth.
The valley bottom surrounding this proposed unit is densely forested, but a network of unpaved roads and oil and gas well sites are located along the ridgetops to the east and west of the stream
ublicly owned in the form of bridge crossings and road easements. This unit helps to maintain the geographical range of the species (population redundancy) and provides opportunity for population growth.
The valley bottom surrounding this proposed unit is densely forested, but a network of unpaved roads and oil and gas well sites are located along the ridgetops to the east and west of the stream. Within proposed Unit 11, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with oil and gas exploration activities, off-road vehicle use, road runoff, canopy loss, logging, and surface coal mining (legacy effects). These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 12: Walker Creek and Tributaries, Lee and Wolfe Counties, Kentucky
Proposed Unit 12 is located between KY 11 and Shumaker Road to the west and KY 2016 to the east in northern Lee County and southwestern Wolfe County. This unit includes 3.9 skm (2.4 smi) of an unnamed tributary of Walker Creek from its headwaters downstream to its confluence with Walker Creek, 2.4 skm (1.5 smi) of Cowan Fork from its headwaters downstream to its confluence with Hell for Certain Creek, 2.0 skm (1.2 smi) of Hell for Certain Creek from the outflow of an unnamed reservoir downstream to its confluence with Walker Creek, 0.8 skm (0.5 smi) of Boonesboro Fork from its headwaters downstream to its confluence with Walker Creek, 2.2 skm (1.4 smi) of Peddler Creek from its headwaters downstream to its confluence with Walker Creek, 1.1 skm (0.7 smi) of Huff Cave Branch from its headwaters downstream to its confluence with Walker Creek, and 12.6 skm (7.8 smi) of Walker Creek from its headwaters (reservoir) downstream to its confluence with North Fork Kentucky River. Live Kentucky arrow darters have been captured at several locations within proposed Unit 12 (Thomas 2008, p. 5; Service 2012, pp
its confluence with Walker Creek, 1.1 skm (0.7 smi) of Huff Cave Branch from its headwaters downstream to its confluence with Walker Creek, and 12.6 skm (7.8 smi) of Walker Creek from its headwaters (reservoir) downstream to its confluence with North Fork Kentucky River. Live Kentucky arrow darters have been captured at several locations within proposed Unit 12 (Thomas 2008, p. 5; Service 2012, pp. 1-4), including the Old Fincastle Road low-water crossing, a site upstream near the confluence with Boonesboro Fork, and in the headwaters just upstream of the confluence of Walker Creek with Hell For Certain Creek. This unit is located almost
Land use surrounding this proposed unit is similar to that of Little Fork (proposed Unit 11) and Hell Creek (proposed Unit 13). The valley bottom is densely forested, but numerous unpaved roads, oil and gas well sites, and scattered residences occur along the ridgetops to the east and west of the stream. A narrow, unmaintained dirt road (Walker Creek Road) runs parallel to and east of this unit for its entire length; off-road vehicle use is common. This unit helps to maintain the geographical range of the species (adds population redundancy), contributes to genetic exchange between several streams in the Walker Creek watershed, and likely serves as an important source population in the northern limits of the species' range.
Within proposed Unit 12, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with oil and gas exploration activities, off-road vehicle use, road runoff, canopy loss, and legacy effects of previous oil and gas well development. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 13: Hell Creek and Tributaries, Lee County, Kentucky
Proposed Unit 13 is located between KY 11 and Shumaker Road in northern Lee County
ssociated with oil and gas exploration activities, off-road vehicle use, road runoff, canopy loss, and legacy effects of previous oil and gas well development. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 13: Hell Creek and Tributaries, Lee County, Kentucky
Proposed Unit 13 is located between KY 11 and Shumaker Road in northern Lee County. This unit includes 2.3 skm (1.4 smi) of Miller Fork from its headwaters downstream to its confluence with Hell Creek, 0.7 skm (0.4 smi) of Bowman Fork from its headwaters downstream to its confluence with Hell Creek, 1.9 skm (1.2 smi) of an unnamed tributary of Hell Creek from its headwaters downstream to its confluence with Hell Creek, and 7.1 skm (4.4 smi) of Hell Creek from the outflow of an unnamed reservoir downstream to its confluence with North Fork Kentucky River. Live Kentucky arrow darters have been captured within proposed Unit 13 from the Hell Creek mainstem near the Hell Creek Road low-water crossing and from an unnamed tributary of Hell Creek near the Hell Creek Road low-water crossing (Thomas 2008, p. 5; Service 2012, pp. 1-4). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements.
Land use surrounding this proposed unit is similar to that of Little Fork (proposed Unit 11) and Walker Creek (proposed Unit 12). The valley bottom surrounding this proposed unit is forested, but numerous unpaved roads, oil and gas well sites, and scattered residences occur along the ridgetops to the east and west of the stream. A narrow, unmaintained dirt road runs parallel to and east of proposed Unit 13 upstream of the Hell Creek Road crossing; off-road vehicle use is common. This unit helps to maintain the geographical range of the species (population redundancy) and provides opportunity for population growth
oil and gas well sites, and scattered residences occur along the ridgetops to the east and west of the stream. A narrow, unmaintained dirt road runs parallel to and east of proposed Unit 13 upstream of the Hell Creek Road crossing; off-road vehicle use is common. This unit helps to maintain the geographical range of the species (population redundancy) and provides opportunity for population growth.
Within proposed Unit 13, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with oil and gas exploration activities, off-road vehicle use, road runoff, canopy loss, and legacy effects of previous oil and gas well development. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 14: Big Laurel Creek, Harlan County, Kentucky
Proposed Unit 14 is located off KY 221 and Big Laurel Creek Road in northern Harlan County and includes 9.1 skm (5.7 smi) of Big Laurel Creek from its confluence with Combs Fork downstream to its confluence with Greasy Creek. Live Kentucky arrow darters have been captured from this unit near its confluence with White Oak Branch (Thomas 2008, p. 5; Service 2012, pp. 1-4). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. This unit adds population redundancy at the southeastern edge of the species' range.
The valley bottom and hillsides surrounding proposed Unit 14 are densely forested, but extensive surface coal mining within the watershed has created clearings along the ridgetops and has resulted in five valley (hollow) fills that are located within tributaries of Big Laurel Creek
crossings and road easements. This unit adds population redundancy at the southeastern edge of the species' range.
The valley bottom and hillsides surrounding proposed Unit 14 are densely forested, but extensive surface coal mining within the watershed has created clearings along the ridgetops and has resulted in five valley (hollow) fills that are located within tributaries of Big Laurel Creek. Within proposed Unit 14, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with historical surface coal mining, off-road vehicle use, road runoff, logging, and canopy loss. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 15: Laurel Creek, Leslie County, Kentucky
Proposed Unit 15 is located south of US 421/KY 80 in western Leslie County and includes 4.1 skm (2.6 smi) of Laurel Creek from its confluence with Sandlick Branch downstream to its confluence with Left Fork Rockhouse Creek. A single live Kentucky arrow darter has been captured from this unit, approximately 0.48 skm (0.3 smi) from the confluence with Left Fork Rockhouse Creek (Thomas 2013, pers. comm.). A small portion of this proposed unit is privately owned (0.7 skm (0.5 smi)), but the remainder of the unit is in Federal ownership (administered by DNBF). Land and resource management decisions and activities within the DBNF are guided by DBNF's LRMP (USFS 2004, pp. 1-14). This unit adds population redundancy and provides opportunity for population growth.
The watershed surrounding proposed Unit 15 is entirely forested, with no private residences or other structures. Within proposed Unit 15, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with illegal off-road vehicle use, road runoff, and timber management
lation growth.
The watershed surrounding proposed Unit 15 is entirely forested, with no private residences or other structures. Within proposed Unit 15, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with illegal off-road vehicle use, road runoff, and timber management. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 16: Hell For Certain Creek and Tributaries, Leslie County, Kentucky
Proposed Unit 16 is located off Hell For Certain Road between KY 1482 and KY 257 in northern Leslie County. This unit includes 1.3 skm (0.8 smi) of Cucumber Branch from its headwaters downstream to its confluence with Hell For Certain Creek, 3.1 skm (1.9 smi) of Big Fork from its headwaters downstream to its confluence with Hell For Certain Creek, and 11.4 skm (7.1 smi) of Hell For Certain Creek from its headwaters downstream to its confluence with Middle Fork Kentucky River. Live Kentucky arrow darters have been captured from proposed Unit 16 at multiple locations upstream of its confluence with Big Fork (Thomas 2008, p. 4; Service unpublished data). A portion of this proposed unit is in Federal ownership (administered by DBNF) (4.4 skm (2.8 smi)), but the majority of the unit is in private ownership. For the portion of the unit in Federal ownership, land and resource management decisions and activities within the DBNF are guided by DBNF's LRMP (USFS 2004, pp. 1-14). This unit represents a stronghold for the species
The valley bottom surrounding proposed Unit 16 is narrow (approximately 100 m (328 ft) at its widest) and comprised of a mixture of small farms ( e.g., pasture, hayfields) and scattered residences along Hell For Certain Road. The ridgetops and hillsides are relatively undisturbed and dominated by forest
uided by DBNF's LRMP (USFS 2004, pp. 1-14). This unit represents a stronghold for the species
The valley bottom surrounding proposed Unit 16 is narrow (approximately 100 m (328 ft) at its widest) and comprised of a mixture of small farms ( e.g., pasture, hayfields) and scattered residences along Hell For Certain Road. The ridgetops and hillsides are relatively undisturbed and dominated by forest. Within proposed Unit 16, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with road runoff, inadequate sewage treatment, inadequate riparian buffers, construction and maintenance of county roads, agricultural runoff, illegal off-road vehicle use, logging, and timber management (on DBNF). These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 17: Squabble Creek, Perry County, Kentucky
This proposed unit is located south of KY 28, just downstream of Buckhorn Lake Dam and near the community of Buckhorn in northwestern Perry County. Proposed Unit 17 includes 12.0 skm (7.5 smi) of Squabble Creek from its confluence with Long Fork downstream to its confluence with Middle Fork Kentucky River. Live Kentucky arrow darters have been captured from this unit near its confluence with Big Branch (Service unpublished data). This unit is located almost entirely on private land, except for any small amount that is publicly owned in the form of bridge crossings and road easements. This unit helps to maintain the geographical range of the species and provides opportunity for population growth.
The valley surrounding proposed Unit 17 is narrow (approximately 113 m (370 ft) at its widest) and comprised of a mixture of residences (many in clusters) and small farms ( e.g., pasture, hayfields) scattered along KY 2022, which parallels Squabble Creek for much of its length
ments. This unit helps to maintain the geographical range of the species and provides opportunity for population growth.
The valley surrounding proposed Unit 17 is narrow (approximately 113 m (370 ft) at its widest) and comprised of a mixture of residences (many in clusters) and small farms ( e.g., pasture, hayfields) scattered along KY 2022, which parallels Squabble Creek for much of its length. Ridgetops and hillsides in most of the Squabble Creek valley are relatively undisturbed and dominated by forest; however, surface coal mining has occurred along ridgetops (to the north and south of Squabble Creek) in the downstream half of the drainage.
Within proposed Unit 17, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with road runoff, inadequate sewage treatment, agricultural runoff, inadequate riparian buffers, construction and maintenance of county roads, illegal off-road vehicle use, logging, and historical surface coal mining. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 18: Blue Hole Creek and Left Fork Blue Hole Creek, Clay County, Kentucky
Proposed Unit 18 is located along KY 1524 in southeastern Clay County. This unit includes 1.8 skm (1.1 smi) of Left Fork from its headwaters downstream to its confluence with Blue Hole Creek and 3.9 skm (2.4 smi) of Blue Hole Creek from its confluence with Dry Branch downstream to its confluence with the Red Bird River. Live Kentucky arrow darters have been captured from Unit 18 near the mouth of Cow Hollow (Thomas 2008, p. 4). This unit is entirely in Federal ownership (administered by DNBF). Land and resource management decisions and activities within the DBNF are guided by DBNF's LRMP (USFS 2004, pp. 1-14). This unit comprises a portion of the species' core population within the Red Bird River watershed and contributes to connectivity of streams within the watershed
18 near the mouth of Cow Hollow (Thomas 2008, p. 4). This unit is entirely in Federal ownership (administered by DNBF). Land and resource management decisions and activities within the DBNF are guided by DBNF's LRMP (USFS 2004, pp. 1-14). This unit comprises a portion of the species' core population within the Red Bird River watershed and contributes to connectivity of streams within the watershed.
The watershed surrounding proposed Unit 18 is entirely forested, with no private residences or other structures. The only interruption in the canopy is the KY 1525 corridor, which traverses most of the valley. One additional road, Blue Hole School Road, is located at the headwaters of Blue Hole Creek, leading to a small cemetery site. Blue Hole Creek is 1 of 11 Red Bird River tributaries (proposed Units 18-28) that support Kentucky arrow populations (Thomas 2008, entire; Service 2012, entire). Collectively, these streams represent the largest, most significant cluster of occupied streams and are characterized by intact riparian zones with negligible residential development, high gradients with abundant riffles, cool temperatures, low conductivities (less than 100 µS/cm), and stable channels with clean cobble and boulder substrates (Thomas 2008, p. 4; Service 2014, p. 6).
Within proposed Unit 18, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with road runoff, illegal off-road vehicle use, and timber management (on DBNF). These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 19: Upper Bear Creek and Tributaries, Clay County, Kentucky
Proposed Unit 19 is located along KY 1524 and Upper Bear Creek Road in southeastern Clay County
rse effects ( e.g., siltation, water pollution) associated with road runoff, illegal off-road vehicle use, and timber management (on DBNF). These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 19: Upper Bear Creek and Tributaries, Clay County, Kentucky
Proposed Unit 19 is located along KY 1524 and Upper Bear Creek Road in southeastern Clay County. This unit includes 1.5 skm (1.0 smi) of Left Fork Upper Bear Creek from its headwaters downstream to its confluence with Upper Bear Creek, 0.8 skm (0.5 smi) of Right Fork Upper Bear Creek from its headwaters downstream to its confluence with Upper Bear Creek, and 4.5 skm (2.8 smi) of Upper Bear Creek from its confluence with Left Fork and Right Fork Upper Bear Creek downstream to its confluence with the Red Bird River. Live Kentucky arrow darters have been captured from proposed Unit 19 in two locations downstream of the Left and Right Forks (Thomas 2008, p. 4). A small portion of this unit is privately owned (0.2 skm (0.1 smi)), but the majority of the unit is in Federal ownership (administered by DNBF). Land and resource management decisions and activities within the DBNF are guided by DBNF's LRMP (USFS 2004, pp. 1-14). This unit comprises a portion of the species' core population within the Red Bird River watershed and contributes to connectivity of streams within the watershed.
The watershed surrounding proposed Unit 19 is primarily forested, but a few scattered residences and small farms are located along KY 1524 in the upstream (western) half of the watershed. Upper Bear Creek is 1 of 11 Red Bird River tributaries (proposed Units 18-28) that support Kentucky arrow populations (Thomas 2008, entire; Service 2012, entire). See the description of proposed Unit 18 for more information regarding the characterization of the streams within this drainage
attered residences and small farms are located along KY 1524 in the upstream (western) half of the watershed. Upper Bear Creek is 1 of 11 Red Bird River tributaries (proposed Units 18-28) that support Kentucky arrow populations (Thomas 2008, entire; Service 2012, entire). See the description of proposed Unit 18 for more information regarding the characterization of the streams within this drainage.
Within proposed Unit 19, the Kentucky arrow darter and its habitats may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with road runoff, illegal off-road vehicle use, agricultural runoff, and timber management (on DBNF). These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 20: Katies Creek, Clay County, Kentucky
Proposed Unit 20 is located along Katies Creek Road in southeastern Clay County and includes 5.7 skm (3.5 smi) of Katies Creek from its confluence with Cave Branch downstream to its confluence with the Red Bird River.
The watershed surrounding proposed Unit 20 is entirely forested, with no private residences or other structures. The only interruption in the canopy is the Katies Creek Road corridor, which traverses the valley. Katies Creek is 1 of 11 Red Bird River tributaries (proposed Units 18-28) that support Kentucky arrow populations (Thomas 2008, entire; Service 2012, entire). See the description of proposed Unit 18 for more information regarding the characterization of the streams within this drainage.
Within proposed Unit 20, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with road runoff, illegal off-road vehicle use, logging (on private land), and timber management (on DBNF). These threats are in addition to random effects of drought, floods, or other natural phenomena
hin proposed Unit 20, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with road runoff, illegal off-road vehicle use, logging (on private land), and timber management (on DBNF). These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 21: Spring Creek and Little Spring Creek, Clay County, Kentucky
Proposed Unit 21 is located west of KY 66 in southeastern Clay County. This unit includes 1.0 skm (0.6 smi) of Little Spring Creek from its headwaters downstream to its confluence with Spring Creek and 8.2 skm (5.1 smi) of Spring Creek from its headwaters downstream to its confluence with the Red Bird River. Live Kentucky arrow darters have been captured within proposed Unit 21 approximately 0.2 skm (0.1 smi) upstream of the mouth of Spring Creek (Thomas 2008, p. 4). A portion of this unit is privately owned (3.6 skm (2.2 smi)), but the majority of the unit is in Federal ownership (administered by DNBF). Land and resource management decisions and activities within the DBNF are guided by DBNF's LRMP (USFS 2004, pp. 1-14). This unit comprises a portion of the species' core population within the Red Bird River watershed and contributes to connectivity of streams within the watershed.
The watershed surrounding proposed Unit 21 is relatively undisturbed and dominated by forest; however, a few scattered residences are located along a short segment (approximately 0.8 skm (0.5 smi)) of Lower Spring Creek Road near its junction with KY 66 and along Sand Hill Road and Spring Creek Road at the western (upstream) end of the drainage. The stream corridor between these two areas, an approximate 6.4-skm (4-smi) segment, is inaccessible except by off-road vehicle. About 10 oil wells are located along ridgetops and hillsides near the mouth of Spring Creek, and these sites are connected by a network of unpaved roads
its junction with KY 66 and along Sand Hill Road and Spring Creek Road at the western (upstream) end of the drainage. The stream corridor between these two areas, an approximate 6.4-skm (4-smi) segment, is inaccessible except by off-road vehicle. About 10 oil wells are located along ridgetops and hillsides near the mouth of Spring Creek, and these sites are connected by a network of unpaved roads. Spring Creek is 1 of 11 Red Bird River tributaries (proposed Units 18-28) that support Kentucky arrow populations (Thomas 2008, entire; Service 2012, entire). See the description of proposed Unit 18 for more information regarding the characterization of the streams within this drainage.
Within proposed Unit 21, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with road runoff, off-road vehicle use, inadequate sewage treatment, logging (on private land), timber management (on DBNF), and oil and gas exploration activities. These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 22: Bowen Creek and Tributaries, Leslie County, Kentucky
Proposed Unit 22 is located east of KY 66 and adjacent to Bowen Creek Road in western Leslie County. This unit includes 2.2 skm (1.4 smi) of Laurel Fork from its headwaters downstream to its confluence with Bowen Creek, 1.8 skm (1.1 smi) of Amy Branch from its headwaters downstream to its confluence with Bowen Creek, and 9.6 skm (6.0 smi) of Bowen Creek from its headwaters downstream to the Red Bird River. Live Kentucky arrow darters have been captured from proposed Unit 22 near its confluence with Blevins Branch and Hurricane Branch (Service unpublished data). A portion of this unit is privately owned (2.0 skm (1.2 smi)), but the majority of the unit is in Federal ownership (administered by DNBF). Land and resource management decisions and activities within the DBNF are guided by DBNF's LRMP (USFS 2004, pp. 1-14)
rrow darters have been captured from proposed Unit 22 near its confluence with Blevins Branch and Hurricane Branch (Service unpublished data). A portion of this unit is privately owned (2.0 skm (1.2 smi)), but the majority of the unit is in Federal ownership (administered by DNBF). Land and resource management decisions and activities within the DBNF are guided by DBNF's LRMP (USFS 2004, pp. 1-14). This unit comprises a portion of the species' core population within the Red Bird River watershed and contributes to connectivity of streams within the watershed.
The watershed surrounding this unit is relatively undisturbed and dominated by forest. A few scattered residences are located along Bowen Creek Road near the mid-point of the valley, and others are located further upstream along KY 406. Bowen Creek is 1 of 11 Red Bird River tributaries (proposed Units 18-28) that support Kentucky arrow populations (Thomas 2008, entire; Service 2012, entire). See the description of proposed Unit 18 for more information regarding the characterization of the streams within this drainage.
Within Unit 22, the Kentucky arrow darter and its habitat may require special management considerations or protection to address adverse effects ( e.g., siltation, water pollution) associated with road runoff, illegal off-road vehicle use, inadequate sewage treatment, logging (on private land), and timber management (on DBNF). These threats are in addition to random effects of drought, floods, or other natural phenomena.
Unit 23: Elisha Creek and Tributaries, Leslie County, Kentucky
Proposed Unit 23 is located east of KY 66 and adjacent to Elisha Creek Road in western Leslie County
with ro

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Source: Frix Law Library, https://www.frixlaw.com/law-library/statutes/FR_PRORULE_2015-25290. Check the current official text before relying on it. Not legal advice.