[Federal Register Volume 74, Number 45 (Tuesday, March 10, 2009)]
[Rules and Regulations]
[Pages 10350-10409]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: E9-4536]



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Part II





Department of the Interior





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Fish and Wildlife Service



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50 CFR Part 17



Endangered and Threatened Wildlife and Plants; Designation of Critical 
Habitat for the Louisiana Black Bear (Ursus americanus luteolus); Final 
Rule

  Federal Register / Vol. 74, No. 45 / Tuesday, March 10, 2009 / Rules 
and Regulations  

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DEPARTMENT OF THE INTERIOR

Fish and Wildlife Service

50 CFR Part 17

[FWS-R4-ES-2008-0047; 92210-1117-0000-B4]
RIN 1018-AV52


Endangered and Threatened Wildlife and Plants; Designation of 
Critical Habitat for the Louisiana Black Bear (Ursus americanus 
luteolus)

AGENCY: Fish and Wildlife Service, Interior.

ACTION: Final rule.

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SUMMARY: We, the U.S. Fish and Wildlife Service (Service), designate 
critical habitat for the Louisiana black bear (Ursus americanus 
luteolus) under the Endangered Species Act of 1973, as amended (Act). 
In total, approximately 1,195,821 acres (483,932 hectares) in 
Avoyelles, East Carroll, Catahoula, Concordia, Franklin, Iberia, 
Iberville, Madison, Pointe Coupee, Richland, St. Martin, St. Mary, 
Tensas, West Carroll, and West Feliciana Parishes, Louisiana, fall 
within the boundaries of the critical habitat designation.

DATES: This rule becomes effective on April 9, 2009.

ADDRESSES: This final rule and the associated final economic analysis 
are available on the Internet at http://www.regulations.gov and at 
http://www.fws.gov/lafayette. Supporting documentation we used in 
preparing this final rule is available for public inspection, by 
appointment, during normal business hours, at the U.S. Fish and 
Wildlife Service, Lafayette Ecological Services Field Office, 646 
Cajundome Boulevard, Suite 400, Lafayette, LA 70506; telephone 337-291-
3100; facsimile 337-291-3139.

FOR FURTHER INFORMATION CONTACT: Jim Boggs, Field Supervisor, Lafayette 
Ecological Services Field Office (see ADDRESSES section). If you use a 
telecommunications device for the deaf (TDD), call the Federal 
Information Relay Service (FIRS) at 800-877-8339.

SUPPLEMENTARY INFORMATION: 

Background

    It is our intent to discuss only those topics directly relevant to 
the development and designation of critical habitat for the Louisiana 
black bear in this final rule. For more information on the biology and 
ecology of the Louisiana black bear, refer to the final listing rule 
published in the Federal Register on January 7, 1992 (57 FR 588), and 
to our 1995 final recovery plan, which is available from the Lafayette 
Ecological Services Field Office (see ADDRESSES section). For 
information on Louisiana black bear critical habitat, refer to the 
proposed rule to designate critical habitat for the Louisiana black 
bear published in the Federal Register on May 6, 2008 (73 FR 25354). 
Information on the associated draft economic analysis for the proposed 
rule to designate revised critical habitat was published in the Federal 
Register on November 12, 2008 (73 FR 66831).

Previous Federal Actions

    We listed the Louisiana black bear (Ursus americanus luteolus) as 
threatened under the Act (16 U.S.C. 1531 et seq.) on January 7, 1992 
(57 FR 588). In our final rule listing this subspecies, we determined 
that normal forest management activities supporting a sustained yield 
of timber products and wildlife habitats were compatible with Louisiana 
black bear's needs. Accordingly, we promulgated a special rule under 
section 4(d) of the Act, which can be found at 50 CFR 17.40(i), 
exempting the effects incidental to normal forest management activities 
within the subspecies' historic range, except for activities causing 
damage to or loss of den trees, den tree sites, or candidate den trees 
(57 FR 588). For the purposes of that exemption, normal forest 
management activities are those activities that support a sustained 
yield of timber products and wildlife habitats, thereby maintaining 
forestland conditions in occupied (i.e., breeding) habitat. Research 
has supported this decision. In fact, in some cases, such as leaving 
downed tree tops and creating openings, timber management can provide 
or enhance black bear habitat (Weaver 1999, pp. 126-128; Hightower et 
al. 2002, p. 14; Weaver et al. 1990, p. 344; Lindsey and Meslow 1977, 
p. 424). Therefore, we have not considered changing the special rule at 
50 CFR 17.40.
    We first proposed critical habitat for the Louisiana black bear on 
December 2, 1993 (58 FR 63560), but never published a final rule 
designating critical habitat. On September 6, 2005, Mr. Harold 
Schoeffler and the Louisiana Crawfish Producers Association--West filed 
suit in U.S. District Court for the Western District of Louisiana 
(Civil Action No. CV05-1573 (W.D. La.)) regarding our failure to 
designate critical habitat for the Louisiana black bear.
    On June 26, 2007, the Court ordered the Service to withdraw the 
December 2, 1993, proposed critical habitat rule and create a new 
proposed critical habitat designation by no later than 4 months from 
the date of the judgment and to publish a final designation by no later 
than 8 months from the date of the proposed or new rule. On September 
5, 2007, following a settlement agreement, the Court revised its order 
to require the Service to: (1) Withdraw the December 2, 1993, proposed 
rule and submit a new prudency determination and, if prudent, a new 
proposed critical habitat designation to the Federal Register by April 
26, 2008; and (2) submit a final critical habitat determination, if 
prudent, to the Federal Register by February 26, 2009.
    On May 6, 2008, we proposed critical habitat designation for the 
Louisiana black bear in Avoyelles, Catahoula, Concordia, East Carroll, 
Franklin, Iberia, Iberville, Madison, Pointe Coupee, Richland, St. 
Martin, St. Mary, Tensas, West Carroll, and West Feliciana Parishes, 
Louisiana (73 FR 25354). Simultaneously, we announced our withdrawal of 
the 1993 proposal and our new prudency determination. The proposed rule 
described three units totaling approximately 1,330,000 acres (ac) 
(538,894 hectares (ha)) within Louisiana.
    For more information on previous Federal actions concerning the 
Louisiana black bear, refer to the final rule listing this subspecies 
as threatened published in the Federal Register on January 7, 1992 (57 
FR 588), and the proposed critical habitat rule published in the 
Federal Register on December 2, 1993 (58 FR 63560).

Summary of Comments and Recommendations

    We requested written comments from the public on the proposed 
designation of critical habitat for the Louisiana black bear during two 
comment periods. The first comment period associated with the 
publication of the proposed rule (73 FR 25354) opened on May 6, 2008, 
and closed on July 7, 2008. We also requested comments on the proposed 
critical habitat designation and associated draft economic analysis 
during a comment period that opened November 12, 2008, and closed on 
December 12, 2008 (73 FR 66831). We also contacted appropriate Federal, 
State, and local agencies; scientific organizations; and other 
interested parties and invited them to comment on the proposed rule and 
draft economic analysis during these two comment periods.
    During the first comment period, we received 12 comment letters 
directly addressing the proposed critical habitat designation. During 
the second comment period, we received 15 comment letters addressing 
the proposed critical habitat designation or

[[Page 10351]]

the draft economic analysis. All substantive information provided 
during both comment periods has either been incorporated directly into 
this final determination or addressed below.

Peer Review

    In accordance with our policy published on July 1, 1994 (59 FR 
34270), we solicited expert opinions from five knowledgeable 
individuals with scientific expertise that includes familiarity with 
the subspecies, the geographic region in which the subspecies occurs, 
and conservation biology principles. We received responses from three 
of the peer reviewers.
    We reviewed all comments received from the peer reviewers for 
substantive issues and new information regarding critical habitat for 
the Louisiana black bear. The peer reviewers generally concurred with 
our methods and conclusions and provided additional information, 
clarifications, and suggestions to improve the final critical habitat 
rule. Peer reviewer comments are addressed in the following summary and 
incorporated into the final rule as appropriate.

Peer Reviewer Comments

    (1) Comment: One peer reviewer questioned the permanency of 
perpetual easements purchased through the Wetland Reserve Program (WRP) 
and the process by which such easements could be terminated.
    Our Response: According to the WRP Manual, found in Title II 
(Conservation) of The Farm Security and Rural Investment Act of 2002 
(2002 Farm Bill; Public Law 107-171), prior to making a decision 
regarding easement termination, the Natural Resources Conservation 
Service (NRCS) must: (1) Consult with the Service; (2) investigate 
whether reasonable alternatives to the proposed action exist; and (3) 
determine whether the easement modification is appropriate considering 
the purposes of WRP and the facts surrounding the request for easement 
modification or termination. Any WRP easement modification, including 
termination, must: (1) Be approved by the Director of the NRCS in 
consultation with the Service (the National WRP Program Manager must 
coordinate the consultation with the Service at the national level); 
(2) not adversely affect the wetland functions and values for which the 
easement was acquired; (3) result in equal or greater ecological (and 
economic) values to the U.S. Government; (4) further the purposes of 
the program and address a compelling public need; and (5) comply with 
applicable Federal requirements, including the Act, the National 
Environmental Policy Act (42 U.S.C. 4321 et seq.), Executive Order 
11990 (Protection of Wetlands), and related requirements. At least 90 
days before taking any action to terminate an easement, the Secretary 
of the Department of Agriculture must provide written notice of such 
action to the Committee on Agriculture of the U.S. House of 
Representatives and the Committee on Agriculture, Nutrition, and 
Forestry of the U.S. Senate. Therefore, based on our assessment of 
these requirements, the termination of a WRP easement appears highly 
improbable.
    In addition, our Lafayette Ecological Services Field Office has 
partnered with NRCS to administer WRP in Louisiana since the inception 
of that program in 1992. Following a comprehensive review of our local 
files, and a search of national WRP records, we have been unable to 
find a single instance of a WRP easement being terminated in the 
history of that program (which includes nearly 10,000 projects on 
approximately 2 million ac (800,000 ha) of land nationwide).
    (2) Comment: One peer reviewer expressed concern about the 
potential future conversion of non-WRP forestland to agricultural uses.
    Our Response: Results of recent studies indicate that there has 
been a reversal in the pre-1980s trend of forest conversion to 
agricultural use in the Lower Mississippi River Alluvial Valley (LMAV). 
Documentation of that reversal is limited, however, and a clear 
understanding of the magnitude of afforestation to date has been 
difficult because of the lack of collated data (Schoenholtz et al. 
2001, p. 603). Nonetheless, available data indicates that over the past 
three decades, forest restoration in the LMAV portions of Louisiana, 
Mississippi, and Arkansas has increased dramatically, and has led to a 
significant removal of land from agricultural production for the 
purpose of hardwood forest establishment (Gardiner and Oliver 2005, p. 
243). For example, in the LMAV region of Mississippi, the total 
forested area increased by 11 percent between 1987 and 1994, and 
reforestation of former agricultural lands accounted for nearly 40 
percent of that increase (King and Keeland 1999, p. 352). Between 1993 
and 2007, over 140,000 ac (57,000 ha) were restored to forestland via 
WRP, and 200,000 ac (81,000 ha) via the Conservation Reserve Program, 
within Louisiana black bear habitat priority areas in Louisiana (Ginger 
et al. 2007, p. 41). In summary, there is no evidence that any 
significant amount of forestland will be converted to agriculture in 
the future, and to the contrary, there is a promising trend in the 
annual increase of bottomland hardwood forest (BLH) forestation across 
the LMAV (Schoenholtz et al. 2001, p. 612).
    (3) Comment: One peer reviewer questioned whether bottomland 
hardwoods designated as critical habitat would be considered 
jurisdictional wetlands which would require permit authorization under 
section 404 of the Clean Water Act prior to filling for developmental, 
agricultural, or other purposes. That reviewer also inquired about 
habitat losses and associated impacts to bears should section 404 
permits authorize the loss of forested wetlands within the critical 
habitat boundary.
    Our Response: The U.S. Army Corps of Engineers (Corps) has been 
delegated the authority to regulate the placement of fill in wetlands 
and other waters of the United States. Wetland determination for 
regulatory purposes, such as assessments of wetland losses incurred 
from section 404-permitted activities, is typically done on a project-
specific basis by Corps personnel. Although regional large-scale 
wetland determination maps have not been typically used or developed by 
the Corps for jurisdictional purposes, based on our knowledge of 
forested ecosystems in the LMAV, we believe that most bottomland 
hardwoods within the critical habitat boundary are jurisdictional 
wetlands. Because the Corps evaluates permit applications on an 
individual basis, it would not be possible to determine whether the 
Corps would issue permits and if, or to what extent, they would be 
modified to minimize impacts or to accurately assess the full extent of 
future wetland losses from permitted projects. Given the nature and 
extent of previously permitted activities in bottomland hardwood 
wetlands within this region, we do not anticipate significant habitat 
losses from section 404-permitted projects. Furthermore, the Corps 
requires that section 404 permittees provide compensatory mitigation to 
replace wetland functions and values that are lost via their respective 
projects. Compensatory mitigation area virtually always equals or 
exceeds impacted area and is accomplished within, or in proximity to, 
the watershed of the impact site. Such mitigation, although done 
strictly for wetland replacement, would also provide habitat benefits 
for bears and should exceed habitat losses experienced from permitted 
projects.
    (4) Comment: One peer reviewer stated that we have not been able to

[[Page 10352]]

document female interchange between the Deltic Timber tracts and the 
Tensas River National Wildlife Refuge (TRNWR). Therefore, those 
populations currently function as separate populations and should be 
described as such.
    Our Response: After reevaluating all available information related 
to bear populations and interchange between the Deltic Timber tracts 
and the TRNWR, we agree with this statement and have considered this in 
our analysis. It is more correct to state that the relationship between 
those populations ``may soon begin,'' rather than ``have likely 
begun,'' to function as a single population.
    (5) Comment: One peer reviewer requested that we provide a more 
detailed description of the process used to approximate female bear 
home ranges for our breeding habitat delineation.
    Our Response: Female bear home ranges were determined on a 
population-specific basis using published, telemetry-based research 
(Anderson 1997, p. 37; Beausoleil 1999, p. 60; Marchinton 1995, p. 31; 
Wagner 1995, p. 12; Weaver 1999, p. 70). The average home range sizes 
that were calculated as minimum convex polygons for each population 
were converted to average home range radii. Female locations 
(determined from telemetry data collected for the above-referenced 
studies) were buffered with those population-specific home range radii 
using a geographic information system software package to establish an 
approximate breeding habitat boundary. Minor modifications to that 
boundary were made based on the availability of contiguous habitat and 
the presence of movement barriers (such as large expanses of 
agricultural land or poor-quality habitat, waterways, highways, urban 
development, and other major landscape features).
    (6) Comment: One peer reviewer stated that the estimate of minimum 
habitat size for black bears presented by Cox et al. (1994, p. 50) is 
probably too large for Louisiana black bears due to higher habitat 
quality and more agricultural crop availability for many Louisiana 
black bear populations.
    Our Response: We concur with this statement and did not intend to 
suggest that the Cox et al. (1994) estimate would be used as a basis 
for our habitat requirements assessment. We used known home range sizes 
and habitat requirements for Louisiana black bears, on a population-
specific basis (with emphasis on the TRNWR population as a stable 
population that relies mostly on habitat containing features as 
described by the primary constituent elements (PCE) for survival), to 
determine the minimum required habitat size. Our mention of the Cox et 
al. (1994) publication was only intended to present other research 
findings related to minimum habitat requirements for black bears. 
Consistent with this reviewer's comment, our minimum habitat size 
calculation, as described in our May 6, 2008, proposed rule (73 FR 
25354, p. 25364), yielded an estimate that is significantly smaller 
than that of Cox et al. (1994).
    (7) Comment: One peer reviewer commented on the potential value of 
smaller habitat fragments within larger habitat matrices, and whether 
those smaller forested tracts should be designated as critical habitat 
for the Louisiana black bear.
    Our Response: We concur that smaller habitat patches provide 
benefits for bears, particularly to facilitate movement through 
corridors between populations, when they are components of a larger 
habitat matrix. Based on our review of available scientific literature, 
we determined that habitat fragments as small as 12 ac (5 ha) may be 
sufficient to provide linkage and facilitate movement across a 
fragmented landscape (Pelton and Van Manen 1997, p. 33; Beausoleil et 
al. 2005, pp. 409-410). For that reason, we included ``corridors 
consisting of habitat patches 12 ac (5 ha) or greater in size'' in our 
May 6, 2008, proposed rule to designate critical habitat for the 
Louisiana black bear (73 FR 25354, p. 25363).
    (8) Comment: One peer reviewer requested clarification of our 
definition of an ``actual den tree.''
    Our Response: Specific language affording protection of actual den 
trees was included in the 1992 4(d) rule that was part of the listing 
of the Louisiana black bear as a threatened subspecies (57 FR 588, p. 
593). That rule did not, however, define the criteria to be used for 
determining whether a tree is an ``actual den tree.'' We interpret that 
regulatory language to extend protection to den trees as long as bear 
usage is determinable (i.e., it is recognizable by visual observation 
of the subject tree, or was known to be used in previous denning 
seasons), such that those trees are protected even when bears are not 
actively using them. We determine bear use of a den tree by visual or 
audible confirmation (if it is actively being used), telemetry data, 
and the presence of bear claw marks.
    (9) Comment: One peer reviewer questioned the portion of our 
critical habitat designation strategy that involves maintaining the 
viability of existing populations, stating that he does not believe 
that existing populations have been proven viable.
    Our Response: We concur that existing populations have not been 
proven to have long-term (i.e. , 100 years or more) viability. All 
known breeding populations of Louisiana black bears that were present 
at the time of listing, however, continue to exist more than 15 years 
later. Population estimates for Louisiana black bears at the time of 
listing appear to be lower than what recent research would indicate, 
and there is circumstantial evidence that the population is growing 
(LDWF 2007, p. 22). Therefore, we consider these populations to be 
viable (at least in the near term) for planning purposes related to 
habitat restoration and corridor establishment.
    (10) Comment: One peer reviewer questioned the application of 
habitat requirements for the TRNWR subgroup, which benefits from 
extensive access to adjacent agricultural fields, to the Upper and 
Lower Atchafalaya River Basin (ARB) (Critical Habitat Units 2 and 3) 
populations, which have less opportunity to forage on agricultural 
crops. He asserted that due to agricultural crop availability and use 
by the TRNWR subgroup, a greater land base may be necessary for the two 
ARB populations to compensate for the lack of available agriculture.
    Our Response: We agree that the TRNWR subgroup is situated in an 
area that provides greater access to agricultural crops with higher 
nutritional value (e.g., corn, wheat, and soybeans) than the crops that 
are available for the two ARB populations. The Deltic Timber area in 
the northern portion of the Tensas River Basin (Critical Habitat Unit 
1) is a highly fragmented system of isolated forested tracts 
interspersed within an expansive agricultural landscape. Agricultural 
crops used by bears in this area is well documented and occurs at 
greater rates than for any other subgroup or population of Louisiana 
black bears. It should be noted, however, that even within this TRNWR 
subgroup, agricultural crops used by bears varies greatly by season and 
natural foods comprise most of the diet (by volume) for half of the 
year (Anderson 1997, p. 53). We believe that bears in both ARB 
populations also have access to, and will forage on, agricultural crops 
in their vicinity. Because sugarcane is the most commonly grown crop in 
this region, bears in these populations likely benefit less from the 
use of adjacent agriculture than bears in the TRNWR subgroup. 
Accordingly, we incorporated more PCE-definitional habitat into our 
critical habitat boundary (423,170 ac (171,251

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ha) total for Units 2 and 3) for the two ARB populations than is 
currently inhabited by bears in the TRNWR subgroup (141,868 ac (57, 412 
ha)). As explained in our proposal to designate critical habitat (73 FR 
25354, pp. 25364-25365), because the TRNWR subgroup sustains itself 
throughout much of the year primarily on habitats containing the PCEs, 
and that subgroup is viable, based on the results of population 
viability analyses, that subgroup was used as a model to evaluate the 
minimum habitat requirements for maintenance of long-term population 
viability.
    (11) Comment: One peer reviewer stated that the shared boundary 
(i.e., the corridor) between Units 2 and 3 seems relatively constricted 
and may not be adequate to ensure long-term connectivity and dispersal 
across those two units.
    Our Response: We have reassessed the landscape along the southern 
boundary of Unit 2 and the northern boundary of Unit 3 relative to 
potential travel corridors for bears. As explained in the Methods 
section of this document, increasing the unit width in this region 
would incorporate primarily agricultural fields and urban development, 
and virtually no additional forested habitat. Accordingly, the shared 
boundary of these two units has not been modified from our original 
proposal.
    (12) Comment: One peer reviewer had several questions regarding the 
use of the terms ``occupied at time of listing'' and ``currently 
occupied'' and the basis for critical habitat designation only in 
habitat that was occupied at the time of listing. Also, one public 
commenter expressed similar concerns.
    Our Response: Louisiana black bear resource managers have commonly 
used the term ``occupied'' habitat to indicate areas with physical 
evidence of reproduction (e.g., young, females with young, or lactating 
females). Critical habitat is defined in section 3 of the Act in part 
as the specific areas within the geographical area occupied by a 
species at the time it is listed in accordance with the Act, on which 
are found those physical or biological features: (I) Essential to the 
conservation of the species and (II) which may require special 
management considerations or protection. Therefore, for critical 
habitat designation, we use the term ``occupied'' in a less restrictive 
sense to indicate the subspecies' presence in an area without regard to 
reproductive information (i.e., the transient or permanent presence of 
male or female bears). In order to avoid confusion, we use the term 
``breeding areas'' or ``breeding habitat'' in this document to refer to 
areas with physical evidence of reproduction. We inadvertently used the 
term ``currently occupied'' once in the proposal when we should have 
used the term ``current breeding habitat.'' We have noted this error 
and revised our text.
    Under the Act and its implementing regulations (50 CFR 424.12(e)), 
we can designate critical habitat in areas outside of the geographical 
area occupied by the species at the time it is listed only when (1) the 
inclusion of specific areas occupied at the time of listing defined by 
the essential physical and biological features are not sufficient to 
conserve the species and (2) we determine that those areas outside the 
geographical area occupied by the species are essential for the 
conservation of the species. In preparing this final critical habitat 
designation, we did not find any areas outside of the geographical area 
occupied by the Louisiana black bear at the time of listing that are 
essential for the conservation of the subspecies, and we believe the 
specific areas included in this designation are sufficient to conserve 
the subspecies; therefore, we are not designating areas outside of the 
geographical area occupied by the subspecies.
    (13) Comment: One peer reviewer stated that coastal habitat is not 
superior habitat but that the small number of data points and bear use 
of garbage for food may have affected those estimates.
    Our Response: That statement referenced a speculation made by 
researchers over 10 years ago (Wagner 1995, p. 25). We agree that the 
knowledge we have gained about the coastal population indicates the 
commenter is correct, and we have included that in our discussion.
    (14) Comment: One peer reviewer requested additional information on 
how we will evaluate the cumulative effects of critical habitat 
alteration.
    Our Response: Critical habitat receives protection under section 7 
of the Act through the prohibition against Federal agencies carrying 
out, funding, or authorizing the destruction or adverse modification of 
critical habitat. Section 7 of the Act requires consultation on Federal 
actions that may affect critical habitat. Under section 7 of the Act, 
the Federal action agency must provide an analysis of cumulative 
effects, along with other information, when requesting formal 
consultation. The Service is required to consider cumulative effects of 
a proposed action in formulating our biological opinion. Under the 
provisions of the Act, we determine destruction or adverse modification 
on the basis of whether, with implementation of the proposed Federal 
action, the affected critical habitat would remain functional (or 
retain the current ability for the primary constituent elements to be 
functionally established) to serve its intended conservation role for 
the species.
    (15) Comment: One peer reviewer stated that, through the 
coordinated efforts of Federal, State, and private groups, remarkable 
progress in the protection and restoration of black bear habitat has 
been achieved in Louisiana in the past 10 years and was achieved 
without the benefit of critical habitat designation. The commenter 
wished to congratulate all those involved.
    Our Response: We agree that the progress made in Louisiana black 
bear habitat protection and restoration is noteworthy. We estimate that 
about 600,000 ac (240,000 ha) of land have been restored or protected 
in the bear's range since it was listed in January 1992. This includes 
lands that have been purchased by State and Federal agencies, public 
and private lands protected from development, and privately owned lands 
where bear habitat has been restored. All this was accomplished through 
the voluntary participation of many partners, such as the NRCS and 
other Federal agencies, State agencies in Louisiana and Mississippi, 
the Black Bear Conservation Committee (BBCC), the Louisiana Forestry 
Association, universities, and private citizens. We believe that 
designation of critical habitat will provide benefits in addition to 
those provided through private landowner incentive and conservation 
programs, and will further conservation of this subspecies.
    (16) Comment: Two peer reviewers stated that critical habitat 
designation has the potential to diminish landowner support for 
conservation activities benefitting the Louisiana black bear. One 
suggested that we precede critical habitat designation with a public 
education campaign.
    Our Response: We agree that negative perceptions associated with 
critical habitat designations could potentially alienate the private 
landowners that have been, and continue to be, so vital in the 
Louisiana black bear recovery. As we discuss in the ``State Comments'' 
section and in the ``Benefits of Inclusion'' section of this rule, we 
continue to recognize that designating critical habitat in areas where 
we have partnerships with private landowners that have led to 
conservation or management of listed species may impact landowners and 
future partnerships and conservation efforts.

[[Page 10354]]

Therefore, we have excluded private lands enrolled in the WRP under 
permanent conservation easements from critical habitat designation. 
Furthermore, lands that currently do not contain the physical and 
biological features essential to the conservation of the Louisiana 
black bear do not meet the definition of critical habitat and are not 
designated as critical habitat, nor would they be considered to be such 
if they were restored, or allowed to naturally regenerate, to forested 
habitat subsequent to this designation.
    We also agree that public education regarding critical habitat is 
important. From the beginning of this designation process, we have made 
efforts to inform the public (landowners and public agencies) about 
critical habitat and the designation process through newspapers, fact 
sheets, and informal meetings. We are committed to continuing public 
education about the Louisiana black bear and its critical habitat.
    (17) Comment: Two reviewers stated that our approach was logical 
and reasonable. One commenter indicated that we had thoroughly reviewed 
and appropriately interpreted the most recent scientific literature. 
One commenter indicated that we had designated sufficient quantity and 
quality in a way that encompassed all breeding populations and all 
primary constituent elements.
    Our Response: We appreciate the peer reviewers' positive evaluation 
of the biological and scientific basis for our critical habitat 
determination.
    (18) Comment: One commenter provided suggestions on the consistent 
use of terms, citations, and other grammatical inconsistencies.
    Our Response: We have made those corrections where appropriate and 
necessary in this designation.
    (19) Comment: One peer reviewer stated that he did not consider a 
density of one bear per 686 ac (278 ha) as low (even in the 
southeastern United States) and that, while this density is low when 
compared to densities on the nearby Deltic lands, it was more likely 
slightly higher than average across the Southeast.
    Our Response: We agree and have made this correction.
    (20) Comment: One peer reviewer requested clarification on the 
methods we would use to determine the presence of a breeding population 
in Mississippi.
    Our Response: There have been only three documented occurrences of 
successful reproduction of Louisiana black bears in Mississippi (Ginger 
et al. 2007, p. 34); there is no overlap in the home ranges of the 
three female bears that produced those litters. Based on our analysis 
of over 15 years of Louisiana black bear research and telemetry data, 
we have concluded that an isolated female bear (though she may 
occasionally produce a litter of cubs) does not constitute a breeding 
population. We have determined that a breeding population must consist 
of at least five adult females that are known to have successfully 
reproduced and that have overlapping home ranges. Evaluation of 
existing telemetry data indicates that habitats used by fewer than five 
adult females serve as temporary residences during atypical patterns of 
dispersal (i.e., movement patterns that are most often observed in 
bears translocated during reintroduction programs).
    (21) Comment: One peer reviewer questioned why it might be 
desirable to exclude WRP lands enrolled under a permanent easement.
    Our Response: Due to the level of protection from development 
afforded these lands, and the potential that negative perceptions 
associated with critical habitat designations could potentially 
alienate the private landowners that have been so vital to the 
Louisiana black bear recovery, we have determined that the benefits of 
exclusion outweigh the benefits of inclusion for lands enrolled under 
permanent easements in the WRP. In addition, we believe that this 
determination will not result in the extinction of the Louisiana black 
bear. Please refer to the ``Benefits of Exclusion'' section of this 
rule for further information.

Comments From States

    Section 4(i) of the Act states ``the Secretary shall submit to the 
State agency a written justification for his failure to adopt 
regulation consistent with the agency's comments or petition.'' 
Comments received from State agencies regarding the proposal to 
designate critical habitat for the Louisiana black bear are addressed 
below.
    (22) State Comment: The Louisiana Department of Wildlife and 
Fisheries (LDWF) stated that critical habitat designation is not 
necessary for the successful restoration of the black bear in 
Louisiana.
    Our Response: According to section 4(a)(3) of the Act, the Service 
is required to designate critical habitat for threatened and endangered 
species to the maximum extent prudent and determinable. Also, as a 
result of a lawsuit filed by Harold Schoeffler and Louisiana Crawfish 
Producers-West, we were ordered by the court to designate critical 
habitat, if prudent, for the Louisiana black bear. We have already 
determined that designation of critical habitat is prudent (May 6, 
2008, 73 FR 25354). Therefore, we must designate critical habitat to 
fulfill those statutory and legal obligations.
    (23) State Comment: The LDWF stated that critical habitat 
designation for the Louisiana black bear has the potential to alienate 
private landowners who have habitat upon which the bear depends. They 
furthermore indicated that a cooperative relationship is necessary with 
those landowners in order to collect data and accomplish habitat 
restoration needed for delisting.
    Our Response: We agree with the LDWF that negative perceptions 
associated with critical habitat designations could potentially 
alienate the private landowners that have been and continue to be so 
vital to the Louisiana black bear recovery. We also recognize that the 
significant strides made in habitat restoration for this subspecies are 
in large part due to conservation actions taken by private landowners 
and will continue to be needed to conserve this subspecies. As we 
discuss in the ``Benefits of Inclusion'' section of this rule, we 
continue to recognize that designating critical habitat in areas where 
we have partnerships with private landowners that have led to 
conservation or management of listed species may impact landowners and 
future partnerships and conservation efforts. Therefore, we have 
excluded private lands enrolled under permanent conservation easements 
in the WRP from critical habitat designation. Furthermore, lands that 
currently do not contain features essential for the Louisiana black 
bear's conservation do not meet the definition of critical habitat and 
are not designated as critical habitat, nor would they be considered to 
be such if they were restored, or allowed to naturally regenerate, to 
forested habitat subsequent to this designation. We continue to be 
committed to working on habitat restoration with private landowners in 
the future. See our response to Comment 16 above.
    (24) State Comment: The LDWF and several other commenters stated 
strong support for exempting lands enrolled in the NRCS' WRP program 
from critical habitat designation. They also requested that we consider 
exemptions for other Federal conservation assistance programs including 
the NRCS' Conservation Reserve Program (CRP), the Conservation Reserve 
Enhancement Program (CREP), and the Wildlife Habitat Incentive Program 
(WHIP).

[[Page 10355]]

    Our Response: Under section 4(b)(2) of the Act, in considering 
whether to exclude a particular area from the designation, we must 
identify the benefits of including the area in the designation, 
identify the benefits of excluding the area from the designation, and 
determine whether the benefits of exclusion outweigh the benefits of 
inclusion. If, based on this analysis, we make the determination that 
the benefits of exclusion outweigh the benefits of inclusion, then we 
can exclude the area only if such exclusion would not result in the 
extinction of the species.
    In the case of lands enrolled under a permanent easement in the 
WRP, those easement restrictions provide substantial protection and 
management for the Louisiana black bear and its essential habitat 
features in contrast to the designation of critical habitat, which only 
precludes destruction or adverse modification. We have determined that 
the benefits of exclusion outweigh the benefits of inclusion for lands 
enrolled under permanent easements in the WRP. In addition, we believe 
that this determination will not result in the extinction of the 
Louisiana black bear. Please refer to the ``Exclusions Under Section 
4(b)(2) of the Act'' section of this rule, as well as responses to 
Comments 16 and 23, for further information.
    We share the LDWF's concern and acknowledge the benefits that other 
private landowner incentive and conservation programs (i.e., CRP, CREP, 
WHIP) offer for the Louisiana black bear and other wildlife. However, 
landowners who enroll in those programs are not bound by an easement 
that permanently prohibits development or conversion of those lands. 
Instead, landowners sign an agreement (generally 10 to 15 years in 
duration) and at the end of that agreement those properties may be 
converted to another use. In those instances, the protection provided 
to those lands is not significantly different from that provided via 
critical habitat under section 7 of the Act (i.e., protection from 
adverse modification or destruction). Therefore, while we believe that 
excluding lands enrolled in those conservation agreements may provide 
benefits in terms of maintaining landowner cooperation, we have 
determined not to exclude them from this critical habitat designation.
    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 promote the 
recovery of the species. We continue to be committed to working on 
habitat restoration with private landowners in the future.
    (25) State Comment: The LDWF expressed agreement with the proposed 
critical habitat geographic boundaries. The LDWF also indicated that 
those boundaries are consistent with the most current LDWF telemetry, 
research, and habitat data. In addition, the agency stated that while 
bear sightings may occur throughout Louisiana, the proposed critical 
habitat protects the core breeding populations and the highest quality 
bear habitat.
    Our Response: We appreciate the LDWF's positive evaluation of the 
biological and scientific basis for our critical habitat determination.

Public Comments

    (26) Comment: One commenter stated that he believed the Louisiana 
black bear population to be between 500 and 700 bears.
    Our Response: Current Louisiana black bear population estimates 
vary somewhat among the professional community, primarily due to the 
lack of a reliable and comprehensive estimate. We used every published 
population estimate available (Beausoliel 1999, p. 51; Boerson et al. 
2003, p. 203; Pelton and Van Manen 1997, p. 38; Triant et al. 2004, p. 
653) to support our estimated current population size of 400 to 700 
bears. A more comprehensive population study is currently being 
conducted, but will not be finalized prior to the court-ordered 
deadline for publication of this critical habitat designation.
    (27) Comment: One commenter stated that a map published by the BBCC 
in 2006 indicated that bears had been observed in virtually every 
Louisiana parish. That commenter also discussed potential critical 
habitat designation in specific areas based on anecdotal sighting 
information from locations throughout Louisiana and in portions of 
Arkansas and Mississippi.
    Our Response: We acknowledge that bears have been observed 
throughout Louisiana and in portions of its neighboring States. 
Included in those sightings are confirmed Louisiana black bear 
occurrences in relatively major urban areas such as Abbeville, Bossier 
City, Crowley, Lafayette, and New Iberia. Current breeding habitat and 
corridors linking breeding areas were paramount in the delineation of 
this critical habitat designation. We do not have data to show that 
these specific bear sightings suggested by the commenter, in portions 
of Louisiana, Arkansas, and Mississippi, are part of a resident 
population, within current breeding habitat, or within a suitable 
travel corridor that would warrant designation as critical habitat. 
Therefore, we have not included these areas in our designation of 
critical habitat.
    (28) Comment: One commenter briefly described the significance of 
corridors, expressed concern regarding our designation of corridors 
that only link existing populations, and stated that additional 
corridors in other areas should be considered. Several suggested 
potential corridors were described, including those that would link: 
(1) Felsenthal National Wildlife Refuge (NWR) in south Arkansas to the 
Upper Ouachita NWR in north Louisiana; (2) the Gulf of Mexico to the 
Town of Bogalusa in Louisiana, which would include the Pearl River and 
Old River Wildlife Management Areas (WMA) and the Bogue Chitto NWR; (3) 
Cat Island NWR and Tunica Hills WMA to St. Catherine Creek NWR in 
Mississippi; and (4) east-central Louisiana (i.e., Lasalle and Rapides 
Parish) to Texas via the Red River Alluvial Plain (incorporating 
various State WMAs and U.S. Forest Service parcels).
    Our Response: We concur that corridors perform a significant role 
in the conservation of the Louisiana black bear. Accordingly, we have 
designated corridors between all known breeding populations of the 
Louisiana black bear. We also acknowledge that anecdotal Louisiana 
black bear sighting information exists for various locations throughout 
Louisiana and in portions of its neighboring States. As previously 
explained, such sightings are not always evidence of a resident 
population or of an important (or even suitable) travel corridor that 
would warrant designation as critical habitat. Accordingly, we do not 
believe that the designation of Felsenthal NWR and the Upper Ouachita 
NWR, including a corridor linkage, would further the conservation of 
the Louisiana black bear. Since 2000, over 100 bears (including both 
adult females and cubs) have been captured on White River NWR and 
neighboring lands and reintroduced to Felsenthal NWR. Those bears, 
however, are not considered Louisiana black bears; therefore, the 
regulations implementing the Act and associated critical habitat 
designations would not apply to that population or to Felsenthal NWR. 
There have been occasional bear sightings on the Upper Ouachita NWR, 
which have increased since the initiation of the Felsenthal NWR black 
bear reintroduction program (USFWS 2008,

[[Page 10356]]

pp. 48-50); however, we do not have any evidence of a breeding 
population on Upper Ouachita NWR. Consequently, we do not believe that 
there is justification to warrant designation of Felsenthal NWR (with a 
non-U. a. luteolus population), Upper Ouachita NWR (with no 
population), or a corridor linkage between those properties.
    Although bear sightings are occasionally reported in the Pearl 
River Basin between the Gulf of Mexico to the Town of Bogalusa, there 
is no documented evidence of reproduction of Louisiana black bears 
occurring east of the Mississippi River in Louisiana. Very few bear 
studies have been conducted east of the Mississippi River in Louisiana 
due to the extremely low density of bears in this region. We are aware 
of just one such study, where only one confirmed bear occurrence was 
documented during a 5-month study involving 70 bait stations (Stinson 
1996, p. 12). In addition to the Pearl River Basin not supporting a 
breeding population, it does not form a logical corridor between any 
known populations of Louisiana black bears. Accordingly, we have 
determined that this area does not contain the features essential to 
the conservation of the subspecies; therefore, it was not included 
within our critical habitat boundary.
    Cat Island NWR and Tunica Hills WMA occur within, and St. Catherine 
Creek NWR occurs immediately north of, the Stinson (1996, p. 13) study 
area. As described above, that study confirmed speculations that this 
region supports very few bears. Louisiana black bear reproduction has 
not been documented on any of these lands, and establishing a corridor 
between them would serve little, if any, function for bear 
conservation. Therefore, we have determined that this area does not 
contain the features essential to the conservation of the subspecies, 
and it was not included within our critical habitat boundary.
    Although occasional sightings are reported, there is no evidence 
that Louisiana black bears travel the Red River Alluvial Plain between 
east-central Louisiana (i.e., Lasalle and Rapides Parish) and Texas 
with any frequency. There is also no data to support classification of 
any areas within this region as Louisiana black bear breeding habitat.
    In summary, as stated above, current breeding habitat was paramount 
in this delineation of critical habitat, and was based on known 
locations and home ranges of reproductive females. Corridors linking 
those core breeding areas were also designated based on the best 
available science (primarily telemetry studies) and extensive 
landscape-level habitat analyses which are described in the Methods 
section of our previous proposal May 6, 2008, (73 FR 25354, pp. 25359) 
and in this Final Rule.
    (29) Comment: Several commenters suggested that we evaluate the 
effect of major highways on Louisiana black bear dispersal and habitat 
access. Specific reference was made regarding U.S. Highway 90 (Hwy. 90) 
in St. Mary Parish, Louisiana and U.S. Interstate 20 (I-20) in Madison 
Parish, Louisiana, and their apparent lack of permeability for bear 
movement.
    Our Response: We concur that Hwy. 90 and I-20 are major obstacles 
to intra- and inter-population bear movement. Over the last several 
years, we have organized numerous site inspections and meetings 
involving biologists from both the National Wildlife Refuge System and 
the Ecological Services Divisions of the Service, the LDWF, the 
Louisiana Department of Transportation and Development, the Federal 
Highway Administration (FHWA), private environmental and engineering 
firms, and the BBCC to address issues with highway-associated impacts 
to bears. We have completed a biological opinion on the effects of a 
proposed upgrade of Hwy. 90 to interstate specifications on the 
Louisiana black bear, which included a conservation recommendation that 
the FHWA ``install large mammal/bear crossings at suitable locations 
along the subject reach of Hwy. 90.'' With the assistance of the BBCC, 
private corporations, and major local landowners, we are currently 
developing a large-scale habitat restoration and protection plan to 
address both habitat issues and highway-associated limitations on bear 
conservation in this region of the State. We have designed similar 
plans along I-20, most of which have been successfully implemented, 
primarily through the designation of a WRP Special Project Area. 
Although I-20 in Madison Parish has numerous large bridges over river 
and stream crossings that allow safe passage for bears, we have 
developed and implemented plans to further improve the permeability of 
that roadway for bears. The current critical habitat boundary crosses 
both of the subject roadways (in addition to many others), and we 
believe that it fully reflects our planning and conservation efforts 
and is consistent with these commenters' requests.
    (30) Comment: One commenter stated that a single corridor or series 
of habitat linkages through the Mississippi River Delta and the ARB may 
not be adequate for Louisiana black bear conservation.
    Our Response: We determined that designating all Louisiana black 
bear breeding habitat, including corridors that link those habitats, 
would be sufficient to ensure the conservation of this subspecies. 
Currently, all Louisiana black bear breeding populations occur along 
the Atchafalaya and Lower Mississippi River Alluvial Valleys, as 
reflected in our critical habitat boundary and delineation of 
corridors. We concur with this commenter's general position that a 
single habitat linkage would be insufficient for Louisiana black bear 
conservation purposes. For that reason, we delineated corridors to 
provide sufficient width to incorporate numerous potential travel and 
habitat linkages (e.g., small forested patches and riparian zones along 
streams, sloughs, and bayous) between each of the existing breeding 
populations.
    (31) Comment: One commenter recommended modifications to the 
Louisiana Black Bear Recovery Plan including revisions to estimated 
population increases and home range sizes based on Taylor's (1971) 
estimate for the Upper ARB population. The commenter also suggested 
several specific changes to our critical habitat boundary in the 
context of that Plan.
    Our Response: Louisiana black bear population and home range sizes 
were determined on a population-specific basis from the most recent 
available scientific studies (Anderson 1997, p. 37; Beausoliel 1999, 
pp. 51, 57, 60; Boerson et al. 2003, p. 203; Marchinton 1995, p. 31; 
Pelton and Van Manen 1997, p. 38; Triant et al. 2004, p. 653; Wagner 
1995, p. 12; Weaver 1999, p. 70). We will consider recommended 
modifications to the Louisiana Black Bear Recovery Plan when it is 
updated. We assume that the commenter intends for us to address 
critical habitat suggestions in this final rule rather than in a 
revised recovery plan. Accordingly, recommendations related 
specifically to critical habitat are addressed throughout the Public 
Comments section of this document.
    (32) Comment: Two commenters expressed concern about the effects of 
global climate change and resultant sea level rise on the long-term 
viability of the Lower ARB population and of the corridor that connects 
the Lower and Upper ARB populations of Louisiana black bear.
    Our Response: Our critical habitat designation includes the 
hardwood forests on three south Louisiana salt domes (i.e., Avery 
Island, Weeks Island, and Belle Isle). The elevations of those domes 
far exceed the surrounding landscape, with a maximum elevation

[[Page 10357]]

found on Avery Island at 152 feet (ft) (46 meters (m)) above sea level. 
Within Critical Habitat Unit 3, we have also included hardwood forests 
that are flood-protected by levees and pumps to provide a suitable 
travel and habitat linkage to higher-elevation habitats to the north. 
Within this unit, we have designated a relatively large corridor that 
is, to the best of our mapping capabilities, comprised of habitat 
containing the PCEs. We used the best available science (described in 
detail in the Methods section of this document) to delineate that 
corridor in a manner that would facilitate bear movement between the 
Lower ARB and higher-elevation habitats of the Upper ARB population. We 
will continue our negotiations with the Louisiana Department of 
Transportation and Development (LDOTD) and FHWA regarding highway 
crossings for bears on Hwy. 90 along the subject corridor (previously 
described in detail). We will also continue our participation in the 
development of a large-scale habitat restoration and protection plan to 
address both habitat issues and highway-associated limitations on bear 
conservation in the Lower ARB, which will ensure that the subject 
corridor can fully support dispersal from expanding bear populations 
and the northward migration of bears that may leave coastal habitats 
rendered unsuitable by sea level rise. We believe that delineating this 
critical habitat boundary to include higher-elevation salt dome 
forests, flood-protected forests, and a corridor that provides 
northward dispersal opportunities, in conjunction with our continued 
efforts to resolve highway-associated limitations to bear dispersal 
(including our participation in landscape-level habitat restoration and 
protection planning), is sufficient to address conservation challenges 
for the Louisiana black bear.
    (33) Comment: One commenter recommended that we designate critical 
habitat in all areas that support breeding populations and that we 
include habitat linkages between those populations.
    Our Response: We concur and appreciate this validation of our 
critical habitat designation strategy, which is to include all areas 
that contain features essential to the conservation of the Louisiana 
black bear. We have determined that such areas include breeding habitat 
with connecting corridors, and, in accordance with this recommendation, 
we have included all such areas in our designation.
    (34) Comment: One commenter stated that we are proposing to 
designate critical habitat on too small a portion of the Louisiana 
black bear's present range and that we should be allowed to designate 
critical habitat beyond areas where the subspecies is currently secure.
    Our Response: We are unsure what the commenter means by the term 
``where populations are secure.'' However, for inclusion in a critical 
habitat designation, the habitat within the geographical area occupied 
by the species at the time of listing must contain the physical and 
biological features that are essential to the conservation of the 
species and that may require special management consideration or 
protection. Under the Act, we can designate critical habitat in areas 
outside of the geographical area occupied by the species at the time it 
is listed only when (1) the inclusion of specific areas occupied at the 
time of listing defined by the essential physical and biological 
features are not sufficient to conserve the species; and (2) we 
determine that those areas are essential for the conservation of the 
species.
    As stated above, current breeding habitat was paramount in this 
designation, and was based on known locations and home ranges of 
reproductive females. We are also designating corridors linking those 
core breeding areas based on the best available science (primarily 
telemetry studies) and extensive landscape-level habitat analyses, 
which are described in the Methods section of our previous proposal 
(May 6, 2008, 73 FR 25354, pp. 25359) and in this final rule. We 
determined that those areas are sufficient for the conservation of this 
subspecies.
    (35) Comment: One commenter recommended that we reconsider our 
reduction of the 1993 Louisiana black bear critical habitat 
determination and our exclusion of the eastern portion of the ARB.
    Our Response: We withdrew our 1993 proposal to designate Louisiana 
black bear critical habitat (58 FR 63560) concurrently with the 
publication of our new proposal in 2008 (73 FR 25354). In that latter 
proposal, we explained that the withdrawal was not only to comply with 
a court order, but to consider the significant amount of new 
information available on this subspecies and its habitat since the 
initial proposal published over 15 years ago. At the time of the 
initial critical habitat proposal, the resultant boundary was based on 
information (both biological and geographical) that was limited and 
primarily unpublished and anecdotal in nature. The current critical 
habitat boundary is based on numerous published studies including those 
by Anderson (1997), Beausoliel (1999), Benson (2005), Boerson et al. 
(2003), Hightower et al. (2002), Marchinton (1995), Pelton and Van 
Manen (1997), Stinson (1996), Triant et al. (2004), Van Why (2003), 
Wagner (1995), and Weaver (1999). Those studies have provided new 
insight into Louisiana black bear biology and ecology that was not 
available for our 1993 proposal. Therefore, to use the 1993 critical 
habitat boundary as a basis for our current designation would not be 
incorporating the best available scientific and commercial information. 
Our current boundary includes portions, but not all, of the areas 
proposed in 1993; it also includes additional areas beyond those that 
were initially proposed. This is an entirely new designation, developed 
independently of the 1993 proposal, and it is based on sound scientific 
findings that were unavailable in 1993. We followed these same 
principles in our delineation of the boundary through the ARB. We also 
employed new elevation data and digital mapping technologies (described 
in detail in the ``Criteria Used to Designate Critical Habitat'' 
section of this document) to determine areas within the ARB that are 
most likely to facilitate bear movement between the Upper and Lower ARB 
populations. Our boundary through the ARB does not include all possible 
areas that a bear could travel. It includes lands that, based on recent 
scientific findings and the latest mapping technologies, contain the 
features essential for the conservation of the subspecies.
    (36) Comment: One commenter recommended that we designate critical 
habitat in Mississippi, due to recently documented evidence of 
reproduction, and in Texas, due to reported sightings and the area's 
position within the historic range of the Louisiana black bear.
    Our Response: As described in our response to Comment 20, we have 
determined that Mississippi does not support breeding populations of 
the Louisiana black bear. (The ``Criteria Used to Designate Critical 
Habitat'' section provides additional details regarding the 
classification of breeding habitat.)
    We acknowledge that Louisiana black bear sightings have been 
reported throughout Louisiana and in portions of its neighboring States 
including eastern Texas. As previously explained, such sightings are 
not always evidence of a resident population or of an important (or 
even suitable) travel corridor that would warrant designation as 
critical habitat. Since its listing as a threatened subspecies in 1992, 
there has been no

[[Page 10358]]

documented evidence of Louisiana black bear reproduction in Texas.
    (37) Comment: Two commenters specifically requested that lands 500 
ft (152 m) from the top of the top bank of the Tensas River and lands 
within 1,000 ft (305 m) of the land-side toe of the Mississippi River 
mainline levees be excluded because of future maintenance requirements.
    Our Response: The commenters did not provide sufficient information 
for us to evaluate the benefits of exclusion of those areas. Therefore, 
based on analysis, the protection provided to those lands is not 
significantly different from that provided via critical habitat under 
section 7 of the Act (i.e., protection from adverse modification or 
destruction). Therefore, we have not excluded those lands from critical 
habitat designation for the Louisiana black bear.
    (38) Comment: Numerous commenters, including both private and 
governmental entities, expressed opposition to the designation of 
critical habitat for the Louisiana black bear. Another commenter stated 
that we had exaggerated potential habitat losses in making our 
decision. He also stated his belief that the designation of critical 
habitat for the Louisiana black bear was about compliance with the 
courts and control over land resources and not based on science or the 
needs of the bear. Other commenters questioned the need for critical 
habitat based on increased bear sightings and encounters.
    Our Response: According to section 4(a)(3) of the Act, the Service 
is required to designate critical habitat for threatened and endangered 
species to the maximum extent prudent and determinable. As a result of 
a lawsuit filed by Harold Schoeffler and Louisiana Crawfish Producers--
West, we were issued a September 5, 2007, order from the U.S. District 
Court for the Western District of Louisiana to: (1) Withdraw the 
December 2, 1993, proposed rule and submit a new prudency determination 
and, if prudent, a new proposed critical habitat designation to the 
Federal Register by April 26, 2008; and (2) submit a final critical 
habitat determination, if prudent, to the Federal Register by February 
26, 2009. As set forth in the proposed rule, in fulfilling the Court's 
order, we found that critical habitat was prudent and determinable and 
that designation was prudent (73 FR 25354).
    Furthermore, section 4 of the Act requires that we designate 
critical habitat on the basis of the best scientific and commercial 
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 represent 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.
    In preparing this final critical habitat designation for the 
Louisiana black bear, we reviewed and considered comments from the 
public and peer reviewers on the May 6, 2008, proposed designation of 
critical habitat (73 FR 25354) and the November 12, 2008, draft 
economic analysis (73 FR 66831). We also reviewed the most recent data 
for land ownership and habitat types and reevaluated the information 
and data used in our previous proposal.
    (39) Comment: One commenter pointed out that we listed WRP 
enrollment as 55,000 ac (22,000 ha) while over 219,459 ac (88,811 ha) 
of land in Louisiana have been enrolled in the WRP program.
    Our Response: We agree that over 200,000 ac (81,000 ha) have been 
enrolled in the WRP program Statewide. The 55,000 ac (22,000 ha) we 
reference represent the approximate amount of land enrolled in the WRP 
within the proposed critical habitat boundary only.
    (40) Comment: Two commenters expressed concern about potential 
changes to the current forestry exemption (provided in the final rule 
listing the Louisiana black bear as a threatened subspecies [57 FR 
588]), and the impact on silvicultural activity resulting from 
Louisiana black bear critical habitat designation.
    Our Response: We have not removed or modified the forestry 
exemption as written in the final rule listing the Louisiana black bear 
as a threatened subspecies (January 7, 1992, 57 FR 588). In our May 6, 
2008, proposal to designate critical habitat, we specifically stated 
that research supports our conclusion that normal silviculture (i.e., 
timber management that is consistent with the Louisiana Recommended 
Forestry Best Management Practices) is compatible with Louisiana black 
bear management; therefore, we did not propose any changes to that 
special rule under section 4(d) of the Act (at 50 CFR 17.40[i]) as part 
of this critical habitat designation. It should also be noted that, 
consistent with that special rule, there have been no restrictions, nor 
have there been any consultations under the Act, involving 
silvicultural activity and potential impacts to Louisiana black bears 
in the 16 years that the subspecies has been listed.
    (41) Comment: One commenter stated opposition to the exclusion of 
lands enrolled under a permanent conservation easement in the WRP for 
several reasons and stated that these lands should not be used as a 
justification to curtail critical habitat boundaries. That commenter 
stated that: (1) The proposal is not based on an honest balancing of 
the positive and negative, and the Service acted illegally because it 
never weighed the benefits of designation against the risks of 
designation; (2) the Service cannot use exclusions to undermine 
Congress' established purpose for designating critical habitat; (3) 
excluding WRPs via 16 U.S.C. 1532(b)(4) is not appropriate and case law 
would not support the outcome; (4) the Service presents little or no 
evidence to support its conclusion that critical habitat designation is 
a deterrent to WRP enrollment; (5) private landowners may not have 
voluntarily enrolled into WRP without possible regulatory restrictions; 
and (6) the Service failed to acknowledge that landowners receive an 
incentive, in the form of financial support from the Federal 
government, to enroll in this program. The commenter urged the Service 
to include privately owned land held in conservation easements in our 
critical habitat designation, as these lands are not afforded the same 
level of protection as lands within a critical habitat designation.
    Our Response: We have conducted a review and evaluation of the 
benefits of inclusion and the benefits of exclusion of lands enrolled 
in permanent easement under the WRP as critical habitat for the 
Louisiana black bear. We also presented the economic benefits that 
landowners who enroll in this program receive (approximately $8,000 per 
ac ($3,200 per ha)) (Economic Analysis, 2008; Exhibit 2-1 and p. 4-3). 
Due to the benefit provided by the level of protection from development 
afforded these lands and the potential that negative perceptions 
associated with critical habitat designations could potentially 
alienate the private landowners that have been so vital to continuing 
Louisiana black bear recovery, we have determined that the benefits of 
exclusion outweigh the benefits of inclusion for lands enrolled under 
permanent easements in the

[[Page 10359]]

WRP. Please see section ``Benefits of Exclusion--Permanent Easement 
Wetland Reserve Program Lands'' for a more detailed discussion. 
Furthermore, we have determined that such exclusion would not result in 
the extinction of the Louisiana black bear. Please refer to the 
``Exclusions Under Section 4(b)(2) of the Act'' section of this rule 
for a more detailed discussion. We have not excluded any other lands 
under conservation easements.
    (42) Comment: Several commenters expressed concern that critical 
habitat designation will require consultation for various landowner 
activities and that as a result of those consultations, landowner 
activities will be restricted and the Service will ultimately be 
determining what actions would be allowed.
    Our Response: Only Federal activities that may affect the Louisiana 
black bear or its designated critical habitat require consultation 
under section 7 of the Act. Activities on State, Tribal, local, or 
private lands are subject to the section 7 consultation process only if 
they have a Federal nexus, such as activities requiring a Federal 
permit. Federal actions not affecting listed species or critical 
habitat, and actions on State, Tribal, local or private lands that are 
not federally funded, authorized, or permitted, do not require section 
7(a)(2) consultations. Please see ``Section 7 Consultation'' for a more 
detailed discussion.
    (43) Comment: One commenter requested that the Service consider 
possible economic benefits resulting from the designation, specifically 
noting potential benefits resulting from flood control and wetland 
conservation.
    Our Response: As discussed in section 1.3.3 of the draft economic 
analysis (DEA), the Service believes that the direct benefits of the 
proposed rule are best expressed in biological terms that can be 
weighed against the expected cost impacts of the rulemaking. Where data 
are available to evaluate the ancillary benefits of critical habitat 
designation, the analysis may attempt to quantify these benefits (see 
section 1.3.3 of the DEA).
    As noted in section 2.1 of the DEA, land use patterns in the areas 
proposed for critical habitat have been and continue to be shaped by 
Federal flood control programs in addition to local economic factors. 
Specifically, the DEA notes that there are substantial baseline factors 
that provide for conservation of wetlands and provide for flood control 
within the proposed critical habitat areas.
    The DEA considers whether additional changes in land use and 
management, above and beyond baseline conditions, would occur as a 
result of designation. For example, the DEA considers whether the 
designation would result in modifications to oil and gas development 
activities in the context of U.S. Army Corps of Engineers' section 404 
permitting activities (Chapter 3). These potential modifications 
include relocation of drill sites and directional drilling, both of 
which could reduce the impact of this land use on wetlands. However, 
the extent of wetland impact avoided (e.g., amount of area and time 
period), the nature of the avoided impacts, and the resultant benefits 
associated with wetland protection, including flood control benefits, 
cannot be forecast using best available information. In addition, there 
are no data or models that would allow development of a forecast of how 
designation will impact the frequency or severity of floods (i.e., how 
land uses will change as a result of the designation and how these 
changes would impact flood frequency or severity).
    In the case of the Louisiana black bear, there have been no 
previous section 7 consultations under the Act related to flood control 
activities. In addition, as discussed in section 2.4 of the DEA, it is 
possible that participation in voluntary conservation programs will 
decline as a result of critical habitat designation, potentially 
leading to a negative impact on wetland conservation and flood control. 
As a result of all of these factors, potential benefits resulting from 
enhanced flood control or wetlands conservation are not quantified in 
the DEA.
    (44) Comment: A commenter notes that designation of critical 
habitat could impact oil and gas development and commercial and 
residential development.
    Our Response: A draft economic analysis (DEA) was made available to 
the public through the notice of availability (NOA) published November 
12, 2008. Chapter 3 of the DEA discusses impacts on oil and gas 
development. Chapter 5 of the DEA discusses potential impacts on 
residential and commercial development.
    (45) Comment: One commenter stated that designation of critical 
habitat can be ``neutral or beneficial'' in promoting participation in 
voluntary conservation agreements. Another commenter stated that 
designation will lead some landowners to stop cooperating in voluntary 
conservation efforts.
    Our Response: Section 2.4 of the DEA provides a detailed discussion 
of the potential for changes in participation in voluntary conservation 
agreements. The DEA concludes there may be fewer landowner enrollments 
in programs like the WRP that provide substantial benefits for bears, 
and as a result, critical habitat designation could result in a 
reduction of the quantity and quality of available bear habitat 
relative to what would have been available without designation. There 
was insufficient information available, however, to quantify this 
potential change.
    (46) Comment: Several commenters stated that potential impacts on 
agricultural activities, including impacts on land uses and land 
values, could be greater than estimated in the DEA. In addition to the 
apiary fencing costs cited in the DEA, commenters believe that 
additional impacts could result from crop depredation, drainage impacts 
(i.e., impacts on the ability to clear farm and parish drainage 
systems), and additional requirements for pesticide registration.
    Our Response: The DEA discusses potential impacts on agricultural 
activities in section 6.1. As noted in that section, damage to bees and 
hives was identified as the most costly agricultural problem associated 
with the Louisiana black bear. While other crop depredation may occur, 
no complaints have been filed with either the Service or the Louisiana 
Department of Wildlife and Fisheries. Therefore, there is little 
information available to gauge the extent or frequency of crop 
depredation and its resulting economic impact.
    While recognizing that many local farmers and landowners may be 
concerned about the possible land-use restrictions, the Service has not 
identified current agricultural practices as a threat to the Louisiana 
black bear. As a result, to date, there have been no consultations 
under section 7 of the Act related to these activities, and no impacts 
are forecast to occur in the DEA.

Summary of Changes From Proposed Rule

    In preparing the final critical habitat designation for the 
Louisiana black bear, we reviewed and considered comments from the 
public and peer reviewers on the May 6, 2008, proposed designation of 
critical habitat (73 FR 25354) and the November 12, 2008, notice of 
availability of the associated draft economic analysis (73 FR 66831). 
We also reviewed the most recent data for land ownership and habitat 
types and reevaluated the information and data used in our previous 
proposal. As a result, we made the following changes to our proposed 
designation:

[[Page 10360]]

    (1) We made corrections to ensure the consistent use of terms, 
citations, and grammar. We also provided clarification on the use of 
the terms ``occupied at time of listing'', ``occupied'', and 
``breeding'' populations.
    (2) We made corrections to the identity of areas under Federal and 
State ownership by including Federal- and State-owned Farmers Home 
Administration (FmHA) tracts. In the proposed rule (73 FR 25354), we 
had incorrectly assigned those tracts to private ownership.
    (3) We made one correction to clarify our description of one 
primary constituent element (PCE). In the proposed rule (73 FR 25354; 
May 6, 2008), we omitted the word ``wide'' for PCE 2(b). That portion 
of the PCE now reads as follows: (b) Forested areas greater than 150 
feet (46 meters) wide along waterways and sloughs and having a 
diversity of plant species and age-classes of sufficient area, quality, 
and configuration, as described in PCE 1 above, to provide dispersal 
habitat between breeding populations to maintain genetic variability 
and promote stable or increasing populations, and to provide habitat 
supporting safe movement, foraging, and denning.
    (4) In our May 6, 2008, proposed rule we identified 1,331,635 ac 
(538,894 ha) of habitat containing features essential for Louisiana 
black bear conservation in three units (73 FR 25354). As we continued 
work on the proposed designation, we made one change that affected the 
total area considered to meet the definition of critical habitat. We 
refined our mapping accuracy to better define habitat that contains 
essential features to minimize the inclusion of areas that do not 
contain PCEs for the Louisiana black bear, based primarily on a 
reevaluation of the information and data used in our proposal. This 
meant that, to the best extent possible, we removed areas that do not 
contain the PCEs and are not otherwise considered to provide features 
essential to the Louisiana black bear's conservation. Consequently, we 
delineated a boundary that more accurately reflects telemetry data and 
known breeding habitat. No changes were made as a result of the refined 
mapping to the proposed critical habitat boundaries of Units 1 and 2. 
However, we identified lands within the proposed boundary for Unit 3 
that do not contain the PCEs, including urban development, agricultural 
land, and poor-quality non-PCE habitats such as marsh and semi-
permanently inundated swamps that do not link higher quality habitats. 
Although we are reporting a decrease in the overall area of Unit 3, 
removal of those areas has not reduced the extent of habitat containing 
the PCEs in this unit. This refinement resulted in a decrease of 85,516 
ac (34,607 ha) in Unit 3. As a result, we determined that 133,636 ac 
(54,080 ha) in Unit 3 meet the definition of critical habitat.
    (5) In the proposed rule (73 FR 25354; May 6, 2008), we stated that 
we were evaluating the sufficiency of the permanent easement protection 
of the restored land from future conversion or development for the 
purpose of possible exclusion of private lands enrolled in the WRP via 
a permanent easement. We have determined that the benefits of excluding 
lands enrolled in a permanent easement under the WRP from critical 
habitat designation outweigh the benefits of including these lands, and 
that their exclusion will not result in extinction of this subspecies. 
Therefore, we are excluding 48,751 ac (19,729 ha) of Unit 1 and 1,547 
ac (626 ha) of Unit 2 under section 4(b)(2) of the Act, and we are 
designating the remaining 628,505 ac (254,347 ha) of land in Unit 1 and 
433,680 ac (175,504 ha) of land in Unit 2 as critical habitat (see 
``Exclusions Under Section 4(b)(2) of the Act'' section of this final 
rule for a detailed discussion of this exclusion).
    Except as previously discussed, our final designation includes all 
areas proposed as critical habitat for the Louisiana black bear (i.e., 
Units 1, 2, and 3), totaling approximately 1,195,821 ac (483,932 ha).

Critical Habitat

    Critical habitat is defined in section 3 of the Act as:
    (i) The specific areas within the geographical area occupied by a 
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) that may require special management considerations or 
protection; and
    (ii) specific areas outside the geographical area occupied by a 
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 the use 
of all methods and procedures that are necessary to bring any 
endangered species or threatened species to the point at which the 
measures provided under 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, 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 prohibition against Federal agencies carrying out, funding, 
or authorizing the destruction or adverse modification of critical 
habitat. Section 7(a)(2) of the Act requires consultation on Federal 
actions may affect 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 government or public to access private 
lands. Such designation does not require implementation of restoration, 
recovery, or enhancement measures by private 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) would apply.
    For inclusion in a critical habitat designation, the habitat within 
the geographical area occupied by the species at the time of listing 
must contain the physical and biological features that are essential to 
the conservation of the species, and be included only if those features 
may require special management consideration or protection. Critical 
habitat designations identify, to the extent known using the best 
scientific data available, habitat areas that provide essential life 
cycle needs of the species (i.e., areas on which are found those 
physical and biological features essential to the conservation of the 
species). Under the Act, we can designate critical habitat in areas 
outside of the geographical area occupied by the species at the time it 
is listed only when we determine that those areas are essential for the 
conservation of the species.
    Section 4 of the Act requires that we designate critical habitat on 
the basis of the best scientific and commercial 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

[[Page 10361]]

guidance to ensure that our decisions represent 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 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, or other unpublished materials and expert opinion or 
personal knowledge.
    Habitat is often dynamic, and species may move from one area to 
another over time. Furthermore, 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 promote the recovery of the species.
    Areas that support populations, but are outside the critical 
habitat designation, will continue to be subject to conservation 
actions. They are also subject to the regulatory protections afforded 
by the section 7(a)(2) jeopardy standard, as determined on the basis of 
the best available information at the time of the Federal agency 
action. Federally funded or permitted projects affecting listed species 
outside their designated critical habitat areas may still result in 
jeopardy findings in some cases. 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, or other species 
conservation planning efforts if information available at the time of 
these planning efforts calls for a different outcome.

Primary Constituent Elements (PCEs)

    In accordance with section 3(5)(A)(i) of the Act and regulations at 
50 CFR 424.12, in determining which areas occupied by the species at 
the time of listing to designate as critical habitat, we consider those 
physical and biological features essential to the conservation of the 
species that may require special management considerations or 
protection. We consider the physical and biological features to be the 
PCEs laid out in the appropriate quantity and spatial arrangement for 
the conservation of the species. These PCEs 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, and 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 PCEs for the Louisiana black bear from the 
biological needs of this subspecies as described in the Critical 
Habitat section of the proposed rule to designate critical habitat for 
the Louisiana black bear published in the Federal Register on May 6, 
2008 (73 FR 25354).

Space for Individual and Population Growth and Normal Behavior

    Louisiana black bear populations are currently found in the 
bottomland hardwood (BLH) forest communities and associated habitat of 
the Lower Mississippi River Alluvial Valley. Prime black bear habitat 
is characterized by relatively inaccessible terrain, thick understory 
vegetation, and abundant food sources in the forms of shrubs or tree-
borne soft or hard mast (Pelton 1982, p. 507). BLH forest community 
types in the range of the Louisiana black bear, expressed in terms of 
dominance-codominance, include Taxodium distichum (bald cypress); T. 
distichum-Nyssa aquatica (bald cypress-water tupelo); Betula nigra-
Platanus occidentalis (river birch-American sycamore); Populus 
deltoides (cottonwood); Celtis laevigata-Ulmus americana-Fraxinus 
pennsylvanica (sugarberry-American elm-green ash); Quercus nuttallii-U. 
americana-F. pennsylvanica (Nuttall oak-American elm-green ash); 
Q.lyrata-Carya aquatica (overcup oak-water hickory); Liquidambar 
styraciflua-Q. nigra (sweetgum-water oak); and Q. michauxii-Q. falcata 
(swamp chestnut oak-cherrybark oak) (BBCC 1997, p. 15). Benson (2005, 
p. 56, Table 4.1) described habitat types in terms of species, flooding 
regime, and age as: (1) Upland forests--BLH forests in relatively high 
elevation sites not subject to frequent flooding; and (2) lowland 
forest--BLH forests in relatively low elevations subject to seasonal or 
annual flooding. Louisiana black bear habitat in the Lower Atchafalaya 
population differs from the Tensas and Upper Atchafalaya areas in that 
it includes, in addition to forested wetlands (e.g., deciduous forests, 
cypress forests, deciduous and bald cypress forests, shrub-scrub 
marshes), open marshes, deciduous forest spoil banks, and upland 
hardwood forest (Nyland 1995, p. 58). The interspersion of these 
communities may be important in meeting the seasonal needs of the Lower 
Atchafalaya Louisiana black bear (Nyland 1995, p. 58). The coastal (or 
wetland) habitats may provide escape cover, food sources, and secure 
travel corridors between other habitat types (Jones and Pelton 2003, p. 
193).
    The size of the area necessary for black bears may differ depending 
on population density, habitat quality, conservation goals, and 
assumptions regarding minimum viable populations (Rudis and Tansey 
1995, p. 172). For example, Rudis and Tansey (1995, p. 172), citing 
personal communications, reported estimates of minimal areas needed to 
support a black bear population ranging from 79,000 ac (32,000 ha) in 
forested wetlands to 197,684 ac (80, 000 ha) in upland forests. Cox et 
al. (1994, p. 50) estimated that a population of 200 or more bears 
could require a habitat base of approximately 490,000 to 980,000 ac 
(198,000 to 397,000 ha). Maintaining and enhancing key habitat patches 
within breeding habitat is a critical conservation strategy for black 
bears (Hellgren and Vaughan 1994, p. 276). Areas should be large enough 
to maintain female survival rates above the minimum rate necessary to 
sustain a population (Hellgren and Vaughan 1994, p. 280). Weaver (1999, 
pp. 105-106) documented that bear home ranges and movements were 
centered in forested habitat and noted that actions to conserve, 
enhance, and restore that habitat would promote population recovery, 
although no recommendations on minimum requirements were provided. 
Hellgren and Vaughn (1994, p. 283) concluded that large, contiguous 
forests are a critical conservation need for black bears.
    One approach to assessing Louisiana black bear habitat needs is to 
look at existing densities; however, density estimates should be used 
with caution as they can be influenced by population estimation 
methodology and study area delineation. No single area-density 
relationship has been developed for Louisiana black bears; however, 
density estimates have been developed for Louisiana black bears in two 
locations.

[[Page 10362]]

Bear density for the TRNWR subgroup was estimated to be 1 bear per 686 
ac (0.36 per km2). This is low compared to the adjacent 
Deltic subgroup with a density of 1 bear per 173 ac (1.43 per 
km2) (Boersen et al. 2003, p. 204). The unusually high 
densities observed on the Deltic tracts may be the result of the small 
size of the habitat fragments and accessibility of adjacent desirable 
agricultural crops (Boersen et al. 2003, p. 204).
    Another approach to assess Louisiana black bear habitat 
requirements is to examine bear movements and home ranges. The home 
ranges of Louisiana black bears appear to be closely linked to forest 
cover (Marchinton 1995, p. 48). Female range size may be partly 
determined by habitat quality (Amstrup and Beecham 1976, p. 345), while 
male home range size may be determined by the distribution of females 
(i.e., to allow for a male's efficient monitoring of a maximum number 
of females) (Rogers 1987, p. 19). Male black bears commonly disperse, 
and adult male bears can be wide-ranging with home ranges generally 
three to eight times larger than those of adult females (Pelton 1982, 
p. 507) and that may encompass several female home ranges (Rogers 1987, 
p. 19). Dispersal by female black bears is uncommon and typically is a 
short distance (Rogers 1987, p. 43). Females without cubs generally had 
larger home ranges than females with newborn cubs (Benson 2005, p. 46), 
although this difference was observed to vary seasonally, with 
movements more restricted in the spring (Weaver 1999, p. 99). Following 
separation of the mother and yearling offspring, young female black 
bears commonly establish a home range partially within or adjacent to 
their mother's home range (Rogers 1987, p. 39). Young males, however, 
generally disperse from their maternal home range. Limited information 
suggests that subadult males may disperse up to 136 mi (219 km) (Rogers 
1987, p. 44; BBCC 1997, p. 22).
    Home range estimates, calculated as the minimum convex polygon 
(MCP), vary for the Louisiana black bear. The MCP is a way to represent 
animal movement data and is calculated as the smallest (convex) polygon 
that contains all the points a group of animals have visited. Mean MCP 
home range estimates for the Tensas River NWR population were 35,736 ac 
(14,462 ha) and 5,550 ac (2,426 ha) for males and females, respectively 
(Weaver 1999, p. 70). Male home ranges (MCP) in the Upper Atchafalaya 
population may be as high as 80,000 ac (32,375 ha), while female home 
ranges are approximately 8,000 ac (3,237 ha) (Wagner 1995, p. 12). 
Lower Atchafalaya population home ranges (MCP) were estimated to be 
10,477 ac (4,200 ha) for males, and 3,781 ac (1,530 ha) for females 
(Wagner 1995, p. 12). It was speculated that the smaller home ranges of 
Lower Atchafalaya bears when compared to Upper Atchafalaya bears may be 
due to superior habitat quality in the coastal area (Wagner 1995, p. 
25). However, the smaller home range estimates may have been affected 
by the small number of data points and bear use of garbage for food in 
many coastal locations.
    Louisiana black bears located on the Deltic lands in the Tensas 
River population have very small home ranges compared to other black 
bear populations with an estimated average home range (MCP) for males 
of 1,729 ac (700 ha) and 1,038 ac (420 ha) for females (Beausoleil 
1999, p. 57). The smaller home ranges for this population are believed 
to be a result of the bears' reliance on the surrounding agricultural 
crops for forage (Benson 2005, p. 95) and the overall higher quality of 
the forested habitat (Weaver 1999, pp. 90-91). Based on observations of 
the Deltic populations, Benson (2005, p. 95) suggested that it may be 
possible for a relatively large number of bears to require less space 
and persist in limited forest habitat if food is sufficiently abundant 
and diverse.
    Habitat loss, besides reducing the overall area, can result in 
fragmentation or isolation of habitat, as is evident for the Louisiana 
black bear (Clark 1999, p. 107). Habitat fragmentation can restrict 
bear movements both within and between populations (Beausoleil et al. 
2005, p. 403; Marchinton 1995, p. 53; BBCC 1997, p. 23). This can 
result in increased mortality as bears are forced to forage on less 
protected sites, travel farther to forage, or cross barriers such as 
roads (Pelton 1982, p. 507; Hellgren and Maehr 1992, pp. 154, 155, 
156). Open areas, roads, large waterways, development, and large 
expanses of agricultural land may affect habitat contiguity. Such 
features tend to impede the movement of bears (Clark 1999, p. 107). 
Habitat fragmentation also limits the potential for the present 
Louisiana black bear population to expand its current breeding range 
(USFWS 1995, p. 8). Habitat fragmentation can create barriers to 
immigration and emigration that can affect population demographics and 
genetic integrity (Clark et al. 2006, p. 12). Bear populations in a 
relatively large habitat patch are not ensured of long-term survival 
without recolonization by bears from adjacent patches (Clark 1999, p. 
111). The long-term protection of habitat and interconnecting corridors 
or habitat linkages between viable breeding populations is one of the 
recovery criteria for the Louisiana black bear (USFWS 1995, p. 14).
    Habitat linkages or corridors providing vegetative cover can 
facilitate the movement of bears through agricultural (or other open) 
lands, particularly when bears reside in fragmented tracts of forest, 
as is the case for the Louisiana black bear (Weaver et al. 1990b, p. 
347). Based on telemetry locations and visual observations, Marchinton 
(1995, p. 53) determined that wooded drainages were important travel 
corridors for movement between forested tracts. He noted that those 
drainages may facilitate movements across agricultural lands and may be 
important for dispersal. Likewise, Weaver (1999, p. 67) found 
significant black bear use of habitat linkages between larger forested 
tracts, including forested edges associated with bayous, their 
tributaries, various dry ditch bottoms, and brushy ditch and canal 
banks in various agricultural tracts. Bears were also observed to 
frequent certain areas of intact forest such as the banks of rivers, 
sloughs, ditches, and bayous, and Weaver (1999, p. 82) suggested that 
the term ``habitat linkages'' may be more appropriate than travel 
corridors when referring to the remnant habitat features that link 
disjunct wooded tracts.
    Beausoleil (1999, p. 62) observed that female Louisiana black bears 
would not move between woodlots unless they were connected by a 
forested corridor or were closer than 1,640 feet (ft) (0.5 km) apart. 
Anderson (1997, p. 74 via T. Edwards, USFWS pers. communication) found 
that female bears would not travel across expansive agricultural fields 
that separated forested tracts by 4,541 ft (1.3 km) and observed that 
bears traveled along tree-lined ditches that were as narrow as 16 ft (5 
m) in width (Anderson (1997, p. 74). Similarly, Van Why (2003, pp. 30, 
46) observed Louisiana black bears using narrow strips of vegetation 
(less than 33 ft (10 m) in width) to travel through inhospitable 
habitats such as open fields. Weaver et al. (1990b, p. 347) recommended 
a 197-ft (60-m) buffer zone along waterways as a travel corridor or 
habitat linkage. Bears will travel through open habitat (Weaver 1999, 
p. 81), but they may travel farther from the forested edge when in a 
wooded corridor versus in an open field (Anderson 1997, p. 42).
    Habitat linkages, as described in Louisiana black bear population 
studies, are generally described as narrow and linear in shape, most 
likely resulting from the fact that ditches and bayous are

[[Page 10363]]

the only remaining features connecting habitat fragments within a 
population. Non-linear habitat patches located between existing 
populations may also provide areas for bear movement. Such linkages 
increase the amount of forested habitat (Beausoleil et al. 2005, p. 
408) and may serve not only as pathways for concealed travel, but may 
also provide other functions such as escape cover, bedding and denning 
sites, routes for juvenile dispersal, and avenues for genetic exchange 
(Weaver 1999, pp. 82-83). Habitat linkages ranging from 2.5 ac to 12 ac 
(1 ha to 5 ha) can provide cover for black bears (Pelton and Van Manen 
1997, p. 33). Smaller areas (i.e., 2.5 ac (1 ha)) may provide suitable 
movement paths for shorter, within-population movements but may not be 
sufficient for establishing larger movement paths between populations. 
Beausoleil et al. (2005, pp. 409-410) recommended the establishment of 
habitat corridors to reduce the isolation of forested habitats for 
black bears and suggested that corridor width should vary with length 
and increase with distance. Similarly, Cox et al. (1994, p. 35) 
suggested that black bears likely require broader habitat areas rather 
than thin corridors when connecting distant populations.
    While there is scientific discussion regarding the relative 
importance of wildlife corridors in general, they have been shown to be 
important for black bears (Cox et al. 1994, p. 34). Furthermore, in 
modeling spatial landscape structure and species dispersal, King and 
With (2002, p. 33) found that habitat clumping may help mitigate the 
negative effect that habitat loss has on dispersal success. Habitat 
linkages (or corridors) are needed to facilitate bear movement between 
habitat patches within and between black bear populations (Anderson 
1997, p. 82; Wagner 1995, p. 43; BBCC 1997, p. 54). Telemetry data on 
Louisiana black bear movements in the Tensas River Basin demonstrate 
that habitat linkages should be considered in management plans intended 
to ensure Louisiana black bear population viability in fragmented 
habitats and to provide for the large home ranges (particularly of 
males) needed for unimpeded breeding and dispersal (Weaver 1999, p. 
106).

Food, Water, Air, Light, Minerals, or Other Nutritional or 
Physiological Requirements

    The Louisiana black bear's diet is dominated by plant material 
throughout the year (Pelton 1982, p. 508; Anderson 1997, p. 77; Benson 
2005, p. 20). A portion of the diet is made up of animal matter, 
primarily beetles and other insects (which are consumed year-round 
(Anderson 1997, p. 79)), and occasionally carrion (Pelton 1982, pp. 
508-509; Benson 2005, p. 27). Diets vary seasonally in relation to food 
availability as does habitat use (Nyland 1995, p. 53). After den 
emergence in the spring, bears utilize remaining fat reserves (Pelton 
1982, p. 509). As this is generally a time of lower food abundance, 
bears may lose weight but will soon take advantage of any available 
protein-rich foods (Pelton 1982, p. 509). On the Deltic tracts, such 
items include grasses, sedges, oats, wheat, and beetles (Anderson 1997, 
p. 49; Benson 2005, p. 26). During the summer, food abundance and 
diversity increases, and soft mast, found primarily in forest openings, 
becomes a major food source. Soft mast may include such items as 
blackberry, grape, mulberry, sassafras, and paw paw (Weaver et al. 
1990b, p. 344; Anderson 1997, p. 78; BBCC 1997, p. 18; Benson 2005, p. 
26). Recently timbered areas can provide foraging opportunities for 
bears as they allow light penetration through canopy openings and 
provide rotting wood that harbors beetles and grubs (Weaver et al. 
1990b, p. 344). Louisiana black bears were also observed using early 
successional areas (e.g., planted with trees or regenerating naturally) 
planted with trees (0 to 12 years) or by an open canopy and dense 
understory of shrubs, vines, and saplings (Benson 2005, p. 56, Table 
4.1). Such areas provide food and cover similar to natural openings in 
forests.
    Food availability during the late summer and fall is critical as 
bears need to increase their fat stores in preparation for winter 
dormancy and denning (Pelton 1982, p. 509; BBCC 1997, p. 18). Acorns 
and other hard mast are important food items during this period (Pelton 
1986, p. 51; Benson 2005, p. 27). Extensive foraging may occur and 
bears may travel great distances in search of food (Pelton 1982, p. 
509). It is not uncommon for a bear to gain one to two pounds of fat 
daily (Pelton 1986, p. 51). Bears will forage on agricultural crops, 
which may dominate the diet depending on availability (Nyland 1995, p. 
59; Anderson 1997, p. 78; Benson 2005, p. 20).
    An important factor affecting black bear populations appears to be 
variation in food supply and its effect on physiological status and 
reproduction (Rogers 1976, pp. 436-437). Black bear cub survival and 
development are closely associated with the physical condition of the 
mother (Rogers 1976, p. 434). Cub mortality rates and female 
infertility are typically greater in single or successive years of poor 
mast production or failure (Rogers 1987, p. 53; Eiler et al. 1989, p. 
357; Elowe and Dodge 1989, p. 964). Nutrition may affect the age of 
female reproductive maturity and subsequent fecundity (Pelton 1982, p. 
504). Reproduction may occur as early as 2 years of age for black bears 
in high quality habitat; in poor or marginal habitat, reproduction may 
not occur until 7 years of age (Rogers 1987, pp. 51-52, Table 8). 
Litter size may be affected by food availability prior to denning 
(Rogers 1987, p. 53, Table 10). During periods of food shortages, bears 
range farther in search of food. This increased movement substantially 
increases their chances for human encounters and human-related 
mortality (Rogers 1976, p. 436; Pelton 1982, p. 509). These high 
mortality rates are suspected to be greater for yearling and subadult 
black bear males dispersing from the family unit, and are probably the 
result of starvation, accidents (e.g., vehicular collisions), and 
poaching.

Cover or Shelter

    Black bears undergo a period of winter dormancy that allows them to 
circumvent food shortages and severe weather (Pelton 1982, p. 508). 
Louisiana black bears generally enter dens in early December and emerge 
in mid-April (Weaver 1999, p. 116, Table 4.1). They may remain somewhat 
active during this period and have been observed changing den sites and 
foraging, although their home range sizes are reduced (Weaver 1999, p. 
115; Hightower et al. 2002, p. 16). Louisiana black bears use trees, 
brush piles, and ground nests for denning (Weaver 1999, p. 118; 
Hightower et al. 2002, p. 14). An individual bear may use one or more 
different den types, often within the same season (Weaver 1999, p. 
118). Weaver (1999, p. 120) noted that most den trees were bald 
cypress, but also observed bear use of other species such as overcup 
oak and American sycamore. Den tree cavities appeared to result from 
broken tops or limbs and averaged approximately 49 ft (15 m) in height 
(Weaver 1999, p. 121). Den trees primarily occur along permanently 
flooded sloughs, seasonally flooded flats, lakes, bayous, and rivers 
(Weaver 1999, p. 130). Ground dens were located in wooded habitat and 
constructed from stacked palmetto and vegetation arranged in a wreath-
like manner. Many of the wreath-like dens included excavated 
depressions, but those created from stacked palmetto did not (Weaver 
1999, pp. 121-122). Dens were observed in forested habitat and 
constructed against a backdrop such as a felled log, a tree top, or the 
base of a tree (Weaver 1999, p. 122). In the Tensas population,

[[Page 10364]]

13 of 17 dens were located in forested stands that were at least 
partially timbered within the last 5 years (Weaver 1999, p. 122). Brush 
pile dens were observed in residual tree tops that were felled during 
recent timber harvests (Weaver 1999, pp. 122; Hightower et al. 2002, p. 
14). Trees large enough and sufficiently mature to contain useable 
cavities are almost always found in places inaccessible to logging 
(Marchinton 1995, p. 55), or are left standing due to their low 
economic value.
    The importance of high-quality cover for bedding, denning, and 
escape cover increases as forests become smaller and more fragmented, 
and as human encroachment and disturbance in bear habitat increases 
(Pelton 1986, p. 52). The thick understory found in some BLH forests 
and adjacent areas provides high-quality escape cover, which is 
considered especially important where fragmented habitats put bear 
populations in closer proximity to humans. Bears frequently use 
forested areas and scrub-shrub habitat as escape cover and as resting 
sites or ``daybeds'' (Weaver et al. 1990b, p. 347). Daybeds are 
generally shallow, unlined depressions excavated in soft ground or leaf 
litter (Pelton 1982, p. 509; BBCC 2005, p. 13). Secure areas for 
bedding, denning, and escape can be found in cover that limits 
visibility, slows foot travel, and creates noise when traversed (Weaver 
et al. 1990b, p. 347).

Sites for Breeding, Reproduction, or Rearing (or Development) of 
Offspring

    The average age for first female reproduction varies widely across 
black bear studies; however, most describe breeding occurring between 3 
years and 5 years of age (Weaver 1990, p. 5). Breeding occurs in summer 
and the gestation period for black bears is 7 to 8 months (Weaver 1990, 
p. 5). Delayed implantation occurs in the black bear; blastocysts float 
free in the uterus and do not implant until late November or early 
December (Pelton 1982, p. 505). Because of this, pregnant females are 
not subject to the nutritional drain of a developing fetus while they 
forage to increase fat reserves for winter torpor (Weaver 1990, p. 5). 
Additional information on female habitat requirements is described in 
the Space for Individual and Population Growth and Normal Behavior 
discussion above. Females give birth during the denning season. The 
normal litter size is two, although litter sizes of one to four cubs 
(and rarely five) do occur. Cubs are altricial (helpless) at birth 
(Weaver 1990, p. 5) and generally exit the den site with the female in 
April or May. Young bears stay with the female through summer and fall, 
and den with her the next winter. The young disperse in their second 
spring or summer, prior to the female's period of estrus (Pelton 1982, 
p. 505). Estrus starts when the female becomes physiologically capable 
of reproducing again. However, not all females produce cubs every other 
winter; reproduction is related to physiological condition (i.e, female 
bears that do not reach an optimal weight or fat level may not 
reproduce in a given year) (Rogers 1987, p. 51).
    Females give birth while in their winter dens. Den site 
characteristics were described in more detail in the ``Cover or 
Shelter'' discussion above. Secure den sites for reproduction are 
particularly important as the young would not survive without their 
mother should she abandon her den because of disturbance. Benson (2005, 
p. 84) found that female reproductive status affected den type use, as 
females with cubs used trees for dens more frequently than ground dens. 
However, Hightower et al. (2002, p. 14) did not detect differences in 
den type use by females based on their reproductive status.
    Tree dens may be an important component for female reproductive 
success in areas subject to flooding (Hellgren and Vaughan 1989a, p. 
352). Den trees located in cypress swamps would appear to provide an 
increase in security (e.g., decrease in disturbance) compared to ground 
dens. The availability of den trees, however, does not appear to be a 
limiting factor for reproductive success (Weaver and Pelton 1994, p. 
431); den trees may not be necessary for Louisiana black bears if 
flooding and disturbance are minimized (Hightower et al. 2002, p. 15).
    To afford additional protection to denning bears, when we listed 
the Louisiana black bear, we extended legal protection to candidate and 
actual den trees by promulgating a special rule under section 4(d) of 
the Act and found at 50 CFR 17.40(i) (57 FR 588, January 7, 1992). As 
the terms imply, ``actual den tree'' refers to any tree used by a 
denning bear during the winter and early spring seasons. Candidate den 
trees are defined in the final rule as Taxodium distichum (bald 
cypress) and Nyssa sp. (tupelo gum) in occupied Louisiana black bear 
habitat having a diameter at breast height of 36 inches (in) (92 
centimeters (cm)) or greater, with visible cavities, and occurring in 
or along rivers, lakes, streams, bayous, sloughs, or other water 
bodies. Results of recent research involving Louisiana black bears 
indicate that they will use virtually any species of tree for a den 
site (including overcup oak, American elm, sweetgum, water hickory, and 
sycamore), if it meets the minimum diameter and cavity presence 
criteria described above (Hightower et al. 2002, p. 16).

Habitats That Are Protected From Disturbance

    Remoteness is an important spatial feature of black bear habitat. 
In the southeastern United States, remoteness is relative to forest 
tract size and the presence of roads. Examples of remoteness important 
for black bear habitat include: A tract of timberland 0.5 mi (0.8 km) 
from well-maintained roads and development (Rudis and Birdsey 1986, p. 
5), a forested tract of more than 2,500 ac (1,000 ha) (Rudis and Tansey 
1995, p. 172), or a tract with 0.8 mi or less of road per mile\2\ 
(0.5km/km\2\) of forest (Pelton 1986, p. 52). Remote timberlands, by 
this definition, are relatively rare within the historical range of 
black bears and are located primarily in Louisiana (Rudis and Birdsey 
1986, p. 5). Increasing road density increases the likelihood of human 
disturbances, which can limit habitat suitability and use for black 
bears.
    In some cases, where remoteness does not exist, bears are adaptable 
and through changes in behavior can survive and thrive in proximity to 
humans if afforded areas of retreat that ensure little chance of close 
contact or visual encounters. For example, bears may shift home range 
locations in response to increases in road densities (Brody and Pelton 
1989, p. 10). However, in areas of fragmented habitat, behavioral 
adjustments may not be sufficient to offset the negative effects of 
barriers such as roads. Approximately 38 percent of known Louisiana 
black bear mortalities are the result of road kills (Pace et al. 2000, 
p. 368).

Primary Constituent Elements for the Louisiana Black Bear

    Under the Act and its implementing regulations, we are required to 
identify the physical and biological features within the geographical 
area known to be occupied at the time of listing that are essential to 
the conservation of the Louisiana black bear and which may require 
special management considerations or protections. The physical and 
biological features are the primary constituent elements (PCEs) laid 
out in a specific spatial arrangement and quantity to be essential to 
the conservation of the species. All areas designated as critical 
habitat for the Louisiana black bear are occupied, are within the 
subspecies' historic geographic range, and contain sufficient

[[Page 10365]]

PCEs to support at least one life history function.
    Based on our current knowledge of the life history, biology, and 
ecology of the subspecies and the requirements of the habitat to 
sustain the essential life history functions of the subspecies, we have 
determined that Louisiana black bear's PCEs are:
    (1) Breeding habitat (i.e., within or contiguous to the home range 
of females in a core breeding population) consisting of hardwood forest 
areas having a diversity of age, class, and species and containing 
sources of hard mast (acorns and nuts) produced by such species as 
mature oaks, hickories, and pecan, and that may include one or more of 
the following:
    (a) Areas containing soft mast provided by a diversity of plant 
species, including, but not limited to, blackberry, grape, mulberry, 
sassafras, paw paw, etc., occurring primarily in forest openings, on 
spoil banks, and in areas adjacent to forested habitat;
    (b) Areas within forested habitat providing protein sources 
consisting of beetles and other colonial insects found in rotting and 
decaying wood found on the forest floor;
    (c) Grasses and sedges found in forest openings, on spoil banks 
with open canopies, and in vegetated areas adjacent to forested 
habitats; and
    (d) Secure areas for reproduction, winter dormancy, day bedding, 
and escape. These include areas with den trees (e.g., bald cypress, 
overcup oak, American sycamore, etc.); areas with a thick understory, 
shrub-scrub habitat, openings along spoil banks, vegetated areas 
adjacent to forests, or any vegetation that provides cover, limits 
visibility, slows foot travel, or creates noise when traversed; early 
successional forests (0 to 12 years) with an open canopy and dense 
understory of shrubs, vines, and saplings; or areas with vegetation 
such as palmetto, greenbriars, blackberry, dewberry, and downed trees.
    (2) Corridors consisting of:
    (a) Habitat patches 12 acres (5 hectares) or greater in size; or
    (b) Forested areas greater than 150 feet (46 meters) wide along 
waterways and sloughs and having a diversity of plant species and age-
classes of sufficient area, quality, and configuration, as described in 
PCE 1 above, to provide dispersal habitat between breeding populations 
to maintain genetic variability and promote stable or increasing 
populations, and to provide habitat supporting safe movement, foraging, 
and denning.
    As described in the Primary Constituent Elements section, breeding 
habitat (PCE-1) must be interspersed and connected by suitable 
corridors (PCE-2) to allow for movement between core populations.
    This final designation is designed for the conservation of PCEs 
necessary to support the life history functions of the Louisiana black 
bear and the areas containing those PCEs in the appropriate quantity 
and spatial arrangement essential for the conservation of the 
subspecies. Because not all life history functions require all the 
PCEs, not all critical habitat will contain all the PCEs.

Special Management Considerations or Protections

    When designating critical habitat, we assess whether the areas 
occupied by the species at the time of listing contain the features 
that are essential to the conservation of the species, and whether 
these features may require special management consideration or 
protections. As stated in the final listing rule (January 7, 1992; 57 
FR 588), threats to the physical and biological features essential to 
the conservation of the Louisiana black bear include the direct and 
indirect impacts of land clearing or development resulting in habitat 
fragmentation and land use conversion, primarily to agriculture and 
development. Activities that may destroy or adversely modify critical 
habitat are those that alter the PCEs to an extent that the value of 
critical habitat for both the survival and recovery of the Louisiana 
black bear is appreciably reduced. More specifically, such activities 
could reduce the extent of habitat available for foraging, denning, 
escape, reproduction and sheltering within populations, and severely 
limit or prevent dispersal and genetic exchange among populations. 
Examples of actions that have effects on Louisiana black bear habitat 
include, but are not limited to:
    (1) Initiation or expansion of agricultural operations; hydrocarbon 
exploration and development; commercial, industrial, and residential 
development; flood control projects that involve clearing of woody 
vegetation on Corps flowage easement lands; and other activities that 
would require the permanent removal or fragmentation of forested 
wetlands;
    (2) Road construction, large-scale or wide-ranging development, and 
flood-control projects that would result in barriers that are 
impermeable to bears;
    (3) Large-scale, temporary clearing of all woody vegetation on 
flowage easements within the Atchafalaya River Basin to facilitate 
drainage of the Mississippi and Atchafalaya Rivers during 
extraordinarily high water periods. Such activities could temporarily 
eliminate habitat for foraging, denning, escape, reproduction, and 
sheltering within populations occurring in Unit 2, and severely limit 
or prevent dispersal and genetic exchange between populations within 
Units 2 and 3.
    As described in more detail in the unit descriptions below, we find 
that the PCEs within each unit may require special management 
considerations or protection due to threats to the Louisiana black bear 
or its habitat.

Criteria Used To Identify Critical Habitat

    As required by section 4(b)(2) of the Act, we used the best 
scientific data available to designate critical habitat. We only 
designate areas outside the geographical area occupied by a species 
when a designation limited to its present range would be inadequate to 
ensure the conservation of the species (50 CFR 424.12(e)).
    We have acquired and evaluated additional data since our previous 
proposal May 6, 2008 (73 FR 25354), and have revised the critical 
habitat boundary to avoid the inclusion of non-PCE land. All critical 
habitat units discussed in this designation are occupied by the 
Louisiana black bear. We use the term ``occupied'' to indicate the 
subspecies' presence in an area without regard to reproductive 
information (i.e., the transient or permanent presence of male or 
female bears). This is in contrast to the use of this same term by 
Louisiana black bear resource managers who have historically used it to 
indicate areas with physical evidence of reproduction (e.g., young, 
females with young, or lactating females). We use the term ``breeding 
areas or breeding habitat'' to refer to areas with physical evidence of 
reproduction.
    Our conservation strategy is based on a review of the biological 
needs of this subspecies as described in the literature, and the 
recovery strategy outlined in the Louisiana black bear recovery plan. 
In proposing critical habitat, our two-fold strategy is to: (1) Reduce 
the potential for extinction by providing habitat in areas of 
sufficient composition and size to maintain the viability of existing 
reproducing populations (as determined by breeding habitat); and (2) 
ensure the demographic vigor and genetic variability of existing 
populations by providing habitat of sufficient composition and location 
to provide areas of connectivity between adjoining breeding 
populations. The discussion below summarizes the criteria used to

[[Page 10366]]

identify critical habitat. For additional information, refer to the 
proposed critical habitat rule published on May 6, 2008 (73 FR 25354).
    We include land within the critical habitat unit boundaries 
contingent upon that land being occupied at the time of listing and 
containing the physical and biological features essential to the 
conservation of the Louisiana black bear, meaning that it either (1) 
serves as breeding habitat, or (2) serves as an immigration or 
emigration corridor between the core breeding populations.
    We have defined breeding habitat as bottomland and upland hardwood 
forests and adjacent vegetated habitats having a diversity of plant 
species and age-classes with evidence of use by at least five adult 
female bears that have home ranges that partially or completely overlap 
(core areas). An area that is completely or partially within one or 
more of those home ranges, but outside of the core area, as defined 
above, would be considered breeding habitat if it: (1) Has demonstrated 
use (via radio telemetry) of at least one female bear and is larger 
than 5 ac (2 ha) in size; or (2) is larger than 100 ac (40 ha) in size, 
regardless of telemetry confirmation of female presence, and is not 
separated from the breeding habitat core area by a landscape feature 
that may negatively influence natural bear movements (e.g., a State or 
Federal road, or a large waterway). Evaluation of existing telemetry 
data suggests that forest use by fewer than five females is generally 
indicative of temporary residence as a result of dispersal (noted most 
often within, and surrounding, the reintroduction complex).
    Immigration and emigration corridors between existing breeding 
habitats were determined primarily by the distance between existing 
core breeding populations. Corridor boundary width varies and was 
further determined by the following three factors (listed below in 
order of decreasing significance):
    (1) The width necessary to incorporate more than one potential 
habitat linkage. Selection of only one path of habitat linkages would 
not account for the nomadic nature of bears, nor for their spatially 
large habitat requirements, and would assume (likely incorrectly) that 
all bears would select the same path while traveling the significant 
distance that separates existing populations. According to Cox et al. 
(1994, p. 35), ``black bears likely require broader habitat areas 
rather than thin corridors if connecting distant populations is a 
goal.''
    (2) The feasibility of delineating all existing forested areas that 
is suitable for smaller scale movements that occur during immigration 
and emigration between existing populations. Anderson (1997, p. 74 via 
T. Edwards, USFWS, personal communication) found that bears would 
travel along ``tree-lined ditches'' that were as narrow as 16 ft (5 m) 
in width. Delineation of such small linkages (which are often abundant 
and sinuous) that provide connectivity between existing populations is 
not technically feasible.
    (3) The presence of existing landscape features, such as large 
water bodies, and State and Federal highways. Placing critical habitat 
boundaries along large landscape features is preferable because those 
features often affect or direct bear movements (i.e., form the actual 
boundary of such movements) and because large landscape features can be 
clearly defined for regulatory purposes.
    We re-assessed the boundaries of all three critical habitat units 
based on comments received on our original proposal, additional data 
acquired subsequent to that proposal, and the original data used in the 
proposal (73 FR 25354; May 6, 2008) which includes: occurrence data for 
the Louisiana black bear (LDWF, the Service, Louisiana State 
University, and the University of Tennessee); 1998, 2004, 2005, and 
2007 digital raster and digital orthophoto quarter-quadrangles (DOQQ); 
and 1:24,000 scale digital raster graphics (DRG) of the USGS 
topographic quadrangles.
    The nature of the landscape within Unit 1 (i.e., heavily fragmented 
forests) significantly reduces the latitude in delineating that 
boundary because it necessitates the inclusion of virtually all remnant 
forests to ensure that sufficient habitat (i.e., breeding habitat and 
corridors) is incorporated within the critical habitat boundary. Based 
on comments received regarding our May 6, 2008 proposal (73 FR 25354), 
we evaluated the potential for increasing the width of Unit 1 
particularly in the corridor areas between breeding populations. Our 
evaluation concluded that increasing the unit width in this region 
would incorporate primarily agricultural fields and virtually no 
additional forested habitat. Including additional agricultural areas 
within the critical habitat boundary would not be beneficial because 
those areas do not contain features essential to the conservation of 
the subspecies. Accordingly, the boundary of Unit 1 has not been 
modified from our proposal.
    The landscape in the northern portion of Unit 2 resembles that of 
Unit 1 in regard to forest fragmentation, and provides similar 
limitations in delineating critical habitat. The southern portion of 
Unit 2, however, traverses the ARB and presented a distinctive 
challenge in determining the placement of boundaries through an 
expansive (over 600,000 ac [242,812 ha]) and virtually uninterrupted 
forested system. The ARB, from U.S. Interstate 10 along its northern 
boundary to U.S. Highway 90 along its southern boundary, does not 
support reproducing females. We used the original geospatial data sets 
from our previous proposal, and employed additional data to determine 
the areas within the ARB that would most likely facilitate bear 
movement between those two populations. That newer data included Light 
Detection and Ranging (LIDAR) Data, classified digital Landsat imagery, 
and Louisiana black bear habitat selection preference data.
    LIDAR data is derived from a remote sensing system that is used by 
the National Oceanic and Atmospheric Administration and National 
Aeronautics and Space Administration (NASA). Data are collected from a 
transceiver, which is mounted to a fixed wing aircraft that sends and 
receives laser pulses along the surface of the earth (http://www.csc.noaa.gov/products/sccoasts/html/tutlid.htm). The final product 
is a set of longitude, latitude, and elevation positions for every data 
point, from which a digital elevational model of ground surface can be 
generated. LIDAR point data are available for the entire ARB and were 
used to identify higher elevations that would be generally more 
conducive to bear usage (particularly for travel between existing 
populations).
    The Landsat Program uses satellites to capture moderate resolution 
remote-sensing data of the earth's surface. Digital Landsat imagery is 
the product of that program, and is jointly managed by NASA and the 
U.S. Geological Survey (USGS). Several Landsat images for the ARB have 
been preliminarily classified into categories of land and water by the 
USGS--National Wetlands Research Center (Allen et al. 2008). The 
classification approach taken by Allen et al. (2008) in their ongoing 
study uses a tasseled cap (TCAP) transformation to reduce the original 
Landsat data to three transformed bands of brightness, greenness, and 
wetness. Images taken at many different river stages are classified 
into areas of land and water and are then used to demonstrate the range 
of expected inundation with changing river stages. We compared ARB 
inundation and dry land prevalence at a variety of river stages with 
the probability of exceedance of those river stages during each month 
of the year based on stage duration curves that we developed from the 
Corps' Atchafalaya

[[Page 10367]]

River gauge data. Through that comparison, we were able to use images 
that were classified at known river stages to temporally evaluate ARB 
land that could provide suitable travel and dispersal corridors for 
bears (i.e., that would not be inundated), especially during the period 
when dispersal would be most likely to occur.
    Wagner (2003) developed a landscape-scaled habitat selection 
function for two Louisiana black bear populations (Upper and Lower ARB) 
using telemetry data and classified Landsat imagery. He used a TCAP 
transformation, as described above for the USGS study, to classify 
Landsat imagery. Bear habitat selections were evaluated based on a 
comparison of that classification to known telemetry locations. Bear 
habitat preferences within the ARB are not known because very few 
bears, if any, permanently reside within that system. The result of 
Wagner's (2003) study was the development of a GIS-based model that 
predicts bear habitat preferences throughout the ARB, using classified 
imagery and known telemetry locations from the two ARB subpopulations.
    Based on our evaluation of these three data sets, we determined 
that the boundary of Unit 2 sufficiently incorporates the best 
available science and was correctly delineated as shown in our May 6, 
2008, proposal (73 FR 25354). Based on comments we received regarding 
that proposal, we also evaluated the potential for increasing the width 
of the southern boundary of Unit 2, where it connects to Unit 3. 
However, similar to the constraints noted for Unit 1, the prevalence of 
agriculture and urban development in this region of the State precludes 
the incorporation of additional forested habitat in the southernmost 
extent of Unit 2. We have determined that it would not be beneficial or 
justifiable to incorporate large agricultural and urban expanses within 
the critical habitat boundary as those lands do not contain features 
essential to the conservation of the subspecies. Accordingly, the 
boundary of Unit 2 has not been modified from our May 6, 2008, proposed 
rule.
    We have made relatively minor revisions to the Unit 3 boundary 
based on a reevaluation of the information and data used in our 
proposal (73 FR 25354). The result is a boundary that more accurately 
reflects telemetry data and known breeding habitat, and that minimizes 
the inclusion of areas that do not contain PCEs for the Louisiana black 
bear. Areas that have been removed from the previously proposed 
boundary include urban development, agricultural land, and poor-quality 
non-PCE habitats such as marsh and semi-permanently inundated swamps 
that do not link higher quality habitats. Although we are reporting a 
decrease in the overall acreage of Unit 3, removal of those areas has 
not reduced the extent habitat containing the PCEs in this unit.
    All areas designated as critical habitat contain the physical and 
biological features essential to the conservation of the subspecies and 
either: (1) Currently support a breeding population of Louisiana black 
bears; or (2) function as corridors to maintain movement between core 
populations. We have determined that those areas are sufficient to 
conserve the Louisiana black bear.
    When determining the critical habitat boundaries for this final 
rule, we made every effort to avoid including developed areas such as 
lands covered by buildings, pavement, and other structures because such 
lands lack the PCEs for the Louisiana black bear. 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 
lands. Any such structures and the land under them inadvertently left 
inside critical habitat boundaries shown on the maps of this critical 
habitat rule have been excluded by text in this final rule. Therefore, 
a Federal action involving these lands would not trigger section 7 
consultation with respect to critical habitat and the requirement of no 
adverse modification unless the specific action may affect adjacent 
critical habitat.

Final Critical Habitat Designation

    We are designating three units as critical habitat for the 
Louisiana black bear. The critical habitat areas described below 
constitute our best assessment at this time of areas that meet the 
definition of critical habitat. Those three areas are: (1) Tensas River 
Basin, (2) Upper Atchafalaya River Basin, and (3) Lower Atchafalaya 
River Basin.
    Table 1 shows both the lands designated as critical habitat and the 
lands being excluded from critical habitat under section 4(b)(2) of the 
Act. Table 2 summarizes the areas that meet the definition of critical 
habitat for the Louisiana black bear and areas designated as critical 
habitat by land ownership (Table 2).

  Table 1--Areas That Meet the Definition of Critical Habitat for the Louisiana Black Bear, Areas Excluded From
                      This Final Critical Habitat, and Areas Designated as Critical Habitat
  [Total area estimates reflect all land within critical habitat unit boundaries. Acre and hectare values were
computer generated individually using GIS software, rounded to nearest whole number, and then summed. Totals may
                                           not match due to rounding.]
----------------------------------------------------------------------------------------------------------------
                                                                     Area that
                                                                     meets the     Area excluded       Area
                                                                   definition of    from final     designated as
                      Critical habitat unit                          critical        critical        critical
                                                                    habitat in      habitat in      habitat in
                                                                       acres           acres           acres
                                                                    (hectares)      (hectares)      (hectares)
----------------------------------------------------------------------------------------------------------------
1. Tensas River Basin...........................................        677,256          48,751         628,505
                                                                       (274,076)        (19,729)       (254,347)
2. Upper Atchafalaya River Basin................................        435,227           1,547         433,680
                                                                       (176,130)           (626)       (175,504)
3. Lower Atchafalaya River Basin................................        133,636               0         133,636
                                                                        (54,080)  ..............        (54,080)
                                                                 -----------------------------------------------
    Total.......................................................      1,246,119          50,298       1,195,821
                                                                       (504,286)        (20,355)       (483,932)
----------------------------------------------------------------------------------------------------------------


[[Page 10368]]


   Table 2--Area Determined To Meet the Definition of Critical Habitat for the Louisiana Black Bear and Areas
                  Designated as Critical Habitat for the Louisiana Black Bear by Land Ownership
   [Acre and hectare values were computer generated individually using GIS software, rounded to nearest whole
                         number, and then summed. Totals may not match due to rounding.]
----------------------------------------------------------------------------------------------------------------
                                                                                     Local and
                                                    Federal in    State in acres    private in    Total in acres
              Critical habitat unit                    acres        (hectares)         acres        (hectares)
                                                    (hectares)                      (hectares)
----------------------------------------------------------------------------------------------------------------
1. Tensas River Basin...........................        100,649         119,273         408,583         628,505
                                                        (40,731)        (48,268)       (165,348)       (254,347)
2. Upper Atchafalaya River Basin................         15,765          74,187         343,729         433,680
                                                         (6,380)        (30,022)       (139,102)       (175,504)
3. Lower Atchafalaya River Basin................          7,440             737         125,459         133,636
                                                         (3,011)           (298)        (50,771)        (54,080)
                                                 ---------------------------------------------------------------
    Total.......................................        123,854         194,197         877,771       1,195,821
                                                        (50,122)        (78,588)       (355,221)       (483,932)
----------------------------------------------------------------------------------------------------------------

Unit Descriptions

Unit 1: Tensas River Basin

    Unit 1 consists of 628,505 ac (254,347 ha) of Federal, State, and 
privately owned lands in the Tensas River Basin. It includes portions 
of Avoyelles, East Carroll, Catahoula, Concordia, Franklin, Madison, 
Richland, Tensas, West Carroll, and West Feliciana Parishes. Portions 
of this land that meet the definition of critical habitat in this area 
(48,751 ac (19,729 ha)) are enrolled under permanent easements in the 
WRP. We excluded those lands from critical habitat because we 
determined the benefits of excluding these lands outweigh the benefits 
of including these lands in a critical habitat designation. 
Furthermore, exclusion of these lands will not result in the extinction 
of this subspecies (see Table 1 and ``Exclusions Under Section 4(b)(2) 
of the Act'' section of this final rule for a detailed discussion of 
this exclusion).
    This unit was occupied at the time of listing and currently 
provides breeding and corridor habitat for the Louisiana black bear. 
The perimeter of the northern portion of Unit 1 approximately coincides 
with the boundaries of the Deltic Timber tracts, TRNWR, and Big Lake 
Wildlife Management Area (WMA). The perimeter of the southern portion 
of Unit 1 is bounded primarily by the Red River WMA and Three Rivers 
Management Area on the north and east; by the Red River, Bayou 
Jeansonne, and Bayou des Glaises on the west; and by the Lower Old 
River on the south.
    The central portion of this unit serves as a corridor and extends 
from the south boundaries of Big Lake WMA and TRNWR in Franklin and 
Tensas Parishes, to the north boundary of Red River WMA in Concordia 
Parish. The Tensas River and Bayou Cocodrie form most of the western 
boundary of that corridor. The eastern boundary of that corridor 
includes the east property boundary of Buckhorn Wildlife WMA, and 
Louisiana State Highways 573, 566, and 15. This area contains features 
essential to the conservation of the Louisiana black bear because it 
serves as a corridor to maintain habitat linkages for immigration and 
emigration between the existing breeding populations at the northern 
and southern extents of this unit. Two of the three recovery criteria 
listed in the Louisiana black bear recovery plan (USFWS 1995, p. 14) 
specifically state that the eventual delisting of the Louisiana black 
bear is contingent upon the establishment (where absent) and long-term 
maintenance of such corridors. According to Clark (1999, p. 111), the 
stability and long-term viability of disjunct populations may be 
precluded in the absence of such corridors.
    A significant portion of Unit 1 occurs within State and federally 
owned or managed lands that include TRNWR (68,909 ac (27,886 ha)), Big 
Lake WMA (19,587 ac (7,927 ha)), Buckhorn WMA (11,238 ac (4,548 ha)), 
Bayou Cocodrie NWR (13,638 ac (5,519 ha)), Lake Ophelia NWR (17,408 ac 
(7,045 ha)), Red River WMA (43,570 ac (17,632 ha)), Three Rivers WMA 
(29,863 ac (12,085 ha)), and Grassy Lake WMA (13,214 ac (5,348 ha)). 
Habitat restoration within Unit 1 has been primarily accomplished 
through the WRP, which is administered by the NRCS, and through a major 
carbon sequestration/habitat restoration project, initiated by Entergy 
Corporation, the Trust for Public Land, Environmental Synergy, Inc., 
and the Service. Since the Louisiana black bear was listed as a 
threatened subspecies in 1992, approximately 53,487 ac (21,645 ha) of 
marginal agricultural land has been restored in this unit as a result 
of the WRP program; the program includes perpetual protection through 
conservation easements for most such tracts. The State of Louisiana has 
purchased 2,420 ac (979 ha) of Wetland Reserve Program lands as an 
addition to the BuckhornWMA. As part of an ongoing carbon sequestration 
initiative, approximately 10,000 acres of marginal agricultural land 
are planned for purchase, reforestation, and transfer to the Service as 
an addition to the TRNWR. The first phase of this project was completed 
in 2005, and involved reforestation of 2,900 ac (1,174 ha) of land that 
were added to the TRNWR.
    Unit 1 contains PCEs 1 and 2. Threats to this subspecies and its 
habitat that may require special management of the physical and 
biological features essential for the conservation of the subspecies in 
this unit include continued habitat fragmentation (from such sources as 
hydrocarbon exploration and production, transportation development, 
agricultural activities, and urban sprawl), and human-induced mortality 
(such as poaching, vehicle strikes, and nuisance abatement activities) 
which is exacerbated by habitat fragmentation.

Unit 2: Upper Atchafalaya River Basin

    Unit 2 consists of 433,680 ac (175,504 ha) of Federal, State, and 
privately owned lands in the Upper Atchafalaya River Basin. It includes 
portions of Iberia, Iberville, Pointe Coupee, St. Martin, and St. Mary 
Parishes. Portions of this land that meet the definition of critical 
habitat in this area (1,547 ac (626 ha)) are enrolled under permanent 
easements in the WRP. We excluded those lands from critical habitat 
because we determined the benefits of excluding these lands outweigh 
the benefits of including these lands in a critical habitat 
designation. Furthermore, exclusion of these lands will not result in 
the extinction of this subspecies (see Table 1 and ``Exclusions Under 
Section

[[Page 10369]]

4(b)(2) of the Act'' section of this final rule for a detailed 
discussion of this exclusion).
    This unit was occupied at the time of listing and currently 
supports breeding and corridor habitat for the Louisiana black bear. 
The northern half of Unit 2 is bounded primarily by Louisiana Highway 1 
on the north, Louisiana Highway 1 and the East Atchafalaya Basin Flood 
Protection Levee on the east, the Atchafalaya River on the west, and 
U.S. Interstate 10 on the south. The southern portion extends from U.S. 
Interstate 10 in St. Martin Parish to U.S. Highway 90 in St. Mary 
Parish. Its east and west boundaries approximately follow the West 
Atchafalaya Basin Flood Protection Levee and the Atchafalaya River, 
respectively. The southern portion of Unit 2 serves as a corridor to 
maintain immigration and emigration between the existing core breeding 
populations in Unit 3 and in the northern half of this unit. Two of the 
three recovery criteria listed in the Louisiana black bear recovery 
plan (USFWS 1995, p. 14) specifically state that the eventual delisting 
of the Louisiana black bear is contingent upon the establishment (where 
absent) and long-term maintenance of such corridors. According to Clark 
(1999, p. 111), the stability and long-term viability of disjunct 
populations may be precluded in the absence of such corridors.
    Portions of Unit 2 occur within State and federally owned and 
managed lands that include Atchafalaya NWR (15,762 ac (6,379 ha)), 
Bayou Teche NWR (3 ac (1 ha)), Sherburne WMA and the adjacent (State-
managed) Corps-owned Bayou Des Ourses Area (29,883 ac (12,093 ha)), and 
Attakapas Island WMA (26,819 ac (10,854 ha)). Habitat restoration 
within Unit 2 has been relatively limited and primarily accomplished 
through the WRP program. Approximately 1,550 ac (627 ha) of marginal 
agricultural land has been restored in this unit as a result of that 
program; the program includes perpetual protection through conservation 
easements for most such tracts.
    Unit 2 contains PCEs 1 and 2. Threats to the Louisiana black bear 
and its habitat that may require special management of the physical and 
biological features essential for the conservation of the subspecies in 
this unit include continued habitat fragmentation (from such sources as 
hydrocarbon exploration and production, transportation development, 
agricultural activities, and urban sprawl), and human-induced mortality 
(such as poaching, vehicle strikes, and nuisance abatement activities), 
which is exacerbated by habitat fragmentation.

Unit 3: Lower Atchafalaya River Basin

    Unit 3 consists of 133,636 ac (54,080 ha) of Federal, State, and 
privately owned lands in the Lower Atchafalaya River Basin. It lies 
south of U.S. Highway 90 (Hwy. 90) in Iberia and St. Mary Parishes. 
This unit was occupied at the time of listing by the Louisiana black 
bear and currently supports breeding habitat.
    In addition to bottomland hardwood forests, bears within this unit 
also utilize upland hardwood habitats associated with four salt domes 
(Avery, Cote Blanche, Weeks Islands, and Belle Isle) and coastal 
marshes adjacent to those forests. The vast majority of Unit 3 is 
privately owned, with the exception of 7,440 ac ( 3,011 ha) of the 
Bayou Teche NWR, which is unique in that it is the only National 
Wildlife Refuge established specifically for the conservation of the 
Louisiana black bear. The boundaries of Unit 3 approximately coincide 
with U.S. Highway 90 to the north; Avery Island to the west; the Gulf 
Intracoastal Waterway (GIWW) to the south; then southeast along Big Wax 
Bayou, southeast of Belle Isle; then northeast along Big Lacassine 
Bayou to the GIWW; then east along the GIWW; then southeast along Hog 
Bayou; then northeast along the Wax Lake Outlet to the GIWW; and then 
east to the Lower Atchafalaya River.
    A significant acreage of bottomland hardwood forests in private 
ownership not associated with the four salt domes is flood-protected 
via levees, manmade ditches, and pumps. Those flood protection features 
have caused such forests to lose their wetland classification and 
associated regulatory protection under the Clean Water Act (33 U.S.C. 
1251 et seq.). Subsequently, there is continual development along the 
Hwy. 90 corridor within Unit 3, most of which is not subject to Federal 
regulation. The Federal Highway Administration and the Louisiana 
Department of Transportation have proposed an upgrade of U.S. Highway 
90, within this unit, to Interstate Highway System standards as an 
extension of U.S. Interstate Highway 49.
    Unit 3 contains PCE 1. Threats to this subspecies and its habitat 
that may require special management of the physical and biological 
features essential for the conservation of the subspecies in this unit 
include continued habitat fragmentation (from such sources as 
hydrocarbon exploration and production, transportation development, 
agricultural activities, and urban sprawl), and human-induced mortality 
(such as poaching, vehicle strikes, and nuisance abatement activities), 
which is exacerbated by habitat fragmentation.

Effects of Critical Habitat Designation

Section 7 Consultation

    Section 7(a)(2) of the Act requires Federal agencies, including the 
Service, to ensure that actions they fund, authorize, or carry out are 
not likely to destroy or adversely modify critical habitat. Decisions 
by the Fifth and Ninth Circuits Court of Appeals have invalidated our 
definition of ``destruction or adverse modification'' (50 CFR 402.02) 
(see Gifford Pinchot Task Force v. U.S. Fish and Wildlife Service, 378 
F. 3d 1059 (9th Cir. 2004) and Sierra Club v. U.S. Fish and Wildlife 
Service, 245 F.3d 434, 442 (5th Cir. 2001)), and we do not rely on this 
regulatory definition when analyzing whether an action is likely to 
destroy or adversely modify critical habitat. Under the statutory 
provisions of the Act, we determine destruction or adverse modification 
on the basis of whether, with implementation of the proposed Federal 
action, the affected critical habitat would remain functional (or 
retain the current ability for the primary constituent elements to be 
functionally established) to serve its intended conservation role for 
the species.
    If a species is listed or critical habitat is designated, section 
7(a)(2) of the Act requires Federal agencies to ensure that activities 
they authorize, fund, or carry out are not likely to jeopardize the 
continued existence of the species or to destroy or adversely modify 
its critical habitat. If a Federal action may affect a listed species 
or its critical habitat, the responsible Federal agency (action agency) 
must enter into consultation with us. As a result of this consultation, 
we document compliance with the requirements of section 7(a)(2) through 
our issuance of:
    (1) A concurrence letter for Federal actions that may affect, but 
are not likely to adversely affect, listed species or critical habitat; 
or
    (2) A biological opinion for Federal actions that are likely to 
adversely affect listed species or critical habitat.
    When we issue a biological opinion concluding that a project is 
likely to jeopardize the continued existence of a listed species or 
destroy or adversely modify critical habitat, we also provide 
reasonable and prudent alternatives to the project, if any are 
identifiable. We define ``Reasonable and prudent alternatives'' at 50 
CFR 402.02 as

[[Page 10370]]

alternative actions identified during consultation that:
     Can be implemented in a manner consistent with the 
intended purpose of the action,
     Can be implemented consistent with the scope of the 
Federal agency's legal authority and jurisdiction,
     Are economically and technologically feasible, and
     Would, in the Director's opinion, avoid jeopardizing the 
continued existence of the listed species or destroying or adversely 
modifying critical habitat.

Reasonable and prudent alternatives can vary from slight project 
modifications to extensive redesign or relocation of the project. Costs 
associated with implementing a reasonable and prudent alternative are 
similarly variable.
    Regulations at 50 CFR 402.16 require Federal agencies to reinitiate 
consultation on previously reviewed actions in instances where we have 
listed a new species or subsequently designated critical habitat that 
may be affected and the Federal agency has retained discretionary 
involvement or control over the action (or the agency's discretionary 
involvement or control is authorized by law). Consequently, Federal 
agencies may sometimes need to request reinitiation of consultation 
with us on actions for which formal consultation has been completed, if 
those actions with discretionary involvement or control may affect 
subsequently listed species or designated critical habitat.
    Federal activities that may affect the Louisiana black bear or its 
designated critical habitat will require section 7 consultation under 
the Act. Activities on State, Tribal, local, or private lands requiring 
a Federal permit (such as a permit from the Corps under section 404 of 
the Clean Water Act (33 U.S.C. 1251 et seq.) or a permit from us under 
section 10(a)(1)(B) of the Act) or involving some other Federal action 
(such as funding from the Federal Highway Administration, Federal 
Aviation Administration, or the Federal Emergency Management Agency) 
are subject to the section 7 consultation process. Federal actions not 
affecting listed species or critical habitat, and actions on State, 
Tribal, local or private lands that are not federally funded, 
authorized, or permitted, do not require section 7(a)(2) consultations.

Application of the ``Adverse Modification'' Standard

    The key factor related to the adverse modification determination is 
whether, with implementation of the proposed Federal action, the 
affected critical habitat would continue to serve its intended 
conservation role for the species, or would retain its current ability 
for the primary constituent elements to be functionally established. 
Activities that may destroy or adversely modify critical habitat are 
those that alter the PCEs to an extent that appreciably reduces the 
conservation value of critical habitat for the Louisiana black bear. 
Generally, the conservation role of Louisiana black bear critical 
habitat units is to maintain the viability of existing reproducing 
populations and to ensure the demographic vigor and genetic variability 
of existing populations.
    Section 4(b)(8) of the Act requires us to briefly evaluate and 
describe in any proposed or final regulation that designates critical 
habitat those activities involving a Federal action that may destroy or 
adversely modify such habitat, or those activities that may be affected 
by such designation.
    Activities that, when carried out, funded, or authorized by a 
Federal agency, may affect critical habitat and therefore should result 
in consultation for the Louisiana black bear include, but are not 
limited to:
    (1) Actions that would reduce the extent of habitat available for 
population maintenance or expansion or that would negatively alter the 
function of forested corridors, which facilitate genetic exchange 
between existing populations, through the permanent conversion or 
fragmentation of those forested habitats. Such activities could 
include, but are not limited to, initiation or expansion of 
agricultural operations; hydrocarbon exploration and development; 
commercial, industrial, and residential development; flood control 
projects that involve clearing of woody vegetation on Corps' flowage 
easement lands; and other activities that would require the permanent 
removal or fragmentation of forested wetlands.
    (2) Actions that would create significant barriers to movement both 
within and among existing populations. Those activities could reduce 
the availability of habitat for foraging, denning, escape, 
reproduction, and sheltering within populations, and severely limit or 
prevent dispersal and genetic exchange among populations. Such actions 
could include, but are not limited to road construction, large-scale or 
wide-ranging development, and flood-control projects that would result 
in barriers that are impermeable to bears.
    (3) Actions performed by the Corps that would result in significant 
habitat losses on their flowage easement lands within the Atchafalaya 
River Basin. Those activities could include large-scale, temporary 
clearing of all woody vegetation on easement lands to facilitate 
drainage of the Mississippi and Atchafalaya Rivers during 
extraordinarily high water periods. Such activities could temporarily 
eliminate habitat for foraging, denning, escape, reproduction, and 
sheltering within populations occurring in Unit 2, and severely limit 
or prevent dispersal and genetic exchange between populations within 
Units 2 and 3.

Exemptions

Application of Section 4(a)(3) of the Act

    The Sikes Act Improvement Act of 1997 (Sikes Act) (16 U.S.C. 670a) 
required each military installation that includes land and water 
suitable for the conservation and management of natural resources to 
complete an integrated natural resources management plan (INRMP) by 
November 17, 2001. An INRMP integrates implementation of the military 
mission of the installation with stewardship of the natural resources 
found on the base. Each INRMP includes:
     An assessment of the ecological needs on the installation, 
including the need to provide for the conservation of listed species;
     A statement of goals and priorities;
     A detailed description of management actions to be 
implemented to provide for these ecological needs; and
     A monitoring and adaptive management plan.
    Among other things, each INRMP must, to the extent appropriate and 
applicable, provide for fish and wildlife management; fish and wildlife 
habitat enhancement or modification; wetland protection, enhancement, 
and restoration where necessary to support fish and wildlife; and 
enforcement of applicable natural resource laws.
    The National Defense Authorization Act for Fiscal Year 2004 (Pub. 
L. 108-136) amended the Act to limit areas eligible for designation as 
critical habitat. Specifically, section 4(a)(3)(B)(i) of the Act (16 
U.S.C. 1533(a)(3)(B)(i)) now provides: ``The Secretary shall not 
designate as critical habitat any lands or other geographical areas 
owned or controlled by the Department of Defense, or designated for its 
use, that are subject to an integrated natural resources management 
plan prepared under section 101 of the Sikes Act (16 U.S.C. 670a), if 
the Secretary determines in writing that such plan provides a benefit 
to the species for which critical habitat is proposed for 
designation.''

[[Page 10371]]

    There are no Department of Defense lands with a completed INRMP 
within the critical habitat designation.

Exclusions

Application of Section 4(b)(2) of the Act

    Section 4(b)(2) of the Act states that the Secretary must designate 
and revise 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 he determines that the benefits of such 
exclusion outweigh the benefits of specifying such area as part of the 
critical habitat, unless he 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. In making that 
determination, the legislative history is clear that the Secretary has 
broad discretion regarding which factor(s) to use and how much weight 
to give to any factor.
    Under section 4(b)(2) of the Act, in considering whether to exclude 
a particular area from the designation, we must identify the benefits 
of including the area in the designation, identify the benefits of 
excluding the area from the designation, and determine whether the 
benefits of exclusion outweigh the benefits of inclusion. If based on 
this analysis we determine that the benefits of exclusion outweigh the 
benefits of inclusion, then we can exclude the area only if such 
exclusion would not result in the extinction of the species.
    In the following sections, we address a number of general issues 
that are relevant to the exclusions considered in the final rule.

Benefits of Designating Critical Habitat

    The process of designating critical habitat as described in the Act 
requires that the Service identify those lands on which are found the 
physical or biological features essential to the conservation of the 
species that may require special management considerations or 
protection, and those areas outside the geographical area occupied by 
the species at the time of listing that are essential to the 
conservation of the species. In identifying those lands, the Service 
must consider the recovery needs of the species, such that, on the 
basis of the best scientific and commercial data available at the time 
of designation, the habitat that is identified, if managed or 
protected, could provide for the survival and recovery of the species.
    The identification of those areas that are essential for the 
conservation of the species and can, if managed, provide for the 
recovery of a species is beneficial. The process of proposing and 
finalizing a critical habitat rule provides the Service with the 
opportunity to determine the physical and biological features essential 
for conservation of the species within the geographical area occupied 
by the species at the time of listing, as well as to determine other 
areas essential to the conservation of the species. The designation 
process includes peer review and public comment on the identified 
physical and biological features and areas. This process is valuable to 
land owners and managers in developing conservation management plans 
for identified areas, as well as any other occupied habitat or suitable 
habitat that may not be included in the Service's determination of 
essential habitat.
    The consultation provisions under section 7(a)(2) of the Act 
constitute the regulatory benefits of critical habitat. As discussed 
above, Federal agencies must consult with us on actions that may affect 
critical habitat and must avoid destroying or adversely modifying 
critical habitat. Federal agencies must also consult with us on actions 
that may affect a listed species and refrain from undertaking actions 
that are likely to jeopardize the continued existence of the species. 
The analysis of effects to critical habitat is a separate and different 
analysis from that of the effects to the species. Therefore, the 
difference in outcomes of these two analyses represents the regulatory 
benefit of critical habitat. For some species, and in some locations, 
the outcome of these analyses will be similar, because effects on 
habitat will often result in effects on the species. However, the 
regulatory standard is different, as the jeopardy analysis looks at the 
action's impact on survival and recovery of the species and the adverse 
modification analysis looks at the action's effects on the designated 
habitat's contribution to the species' conservation. This will, in many 
instances, lead to different results and different regulatory 
requirements. Thus, critical habitat designations may provide greater 
regulatory benefits to the recovery of a species than would listing 
alone.
    There are two limitations to the regulatory effect of critical 
habitat. First, a consultation is required only where there is a 
Federal nexus (an action authorized, funded, or carried out by any 
Federal agency)--if there is no Federal nexus, the critical habitat 
designation of private lands itself does not restrict actions that 
destroy or adversely modify critical habitat. Second, the designation 
only limits destruction or adverse modification. By its nature, the 
prohibition on adverse modification is designed to ensure that the 
conservation role and function of those areas that contain the physical 
and biological features essential to the conservation of the species or 
of unoccupied areas that are essential to the conservation of the 
species are not appreciably reduced as the result of a Federal action. 
Critical habitat designation alone, however, does not require private 
property owners to undertake specific steps toward recovery of the 
species. Once an agency determines that consultation under section 
7(a)(2) of the Act is necessary, the process may conclude informally 
when the Service concurs in writing that the proposed Federal action is 
not likely to adversely affect critical habitat. However, if we 
determine through informal consultation that adverse impacts are likely 
to occur, then formal consultation is initiated. Formal consultation 
concludes with a biological opinion issued by the Service on whether 
the proposed Federal action is likely to result in destruction or 
adverse modification of critical habitat.
    As stated above, the designation of critical habitat does not 
require that any management or recovery actions take place on the lands 
included in the designation. Even in cases where consultation is 
initiated under section 7(a)(2) of the Act, the end result of 
consultation is to avoid jeopardy to the species or adverse 
modification of its critical habitat or both, but not necessarily to 
manage critical habitat or institute recovery actions on critical 
habitat. Conversely, voluntary conservation efforts implemented through 
management plans institute proactive actions over the lands they 
encompass and are put in place to remove or reduce known threats to a 
species or its habitat; they therefore implement recovery actions. We 
believe that in many instances the regulatory benefit of critical 
habitat is low when compared to the conservation benefit that can be 
achieved through implementing habitat conservation plans (HCPs) under 
section 10 of the Act or other voluntary conservation efforts or 
management plans. The conservation achieved through such plans is 
typically greater than what we achieve through multiple site-by-site or 
project-by-project section 7 consultations involving consideration of 
critical habitat. Management plans commit resources to implement long-
term management and protection for particular habitat for at

[[Page 10372]]

least one and possibly other listed or sensitive species. Section 7 
consultations only commit Federal agencies to preventing adverse 
modification of critical habitat caused by the particular project, and 
they are not committed to provide conservation or long-term benefits to 
areas not affected by the proposed action. Thus, implementation of an 
HCP, voluntary conservation action, or management plan that 
incorporates enhancement or recovery as the management standard may 
often provide as much or more benefit than a consultation for critical 
habitat designation.
    Another benefit of including lands in critical habitat is that 
designation of critical habitat serves to educate landowners, State and 
local governments, and the public regarding the potential conservation 
value of an area. This helps focus and promote conservation efforts by 
other parties by clearly delineating areas of high conservation value 
for the Louisiana black bear. In general, critical habitat designation 
always has educational benefits; however, in some cases, they may be 
redundant with other educational effects. For example, HCPs have 
significant public input and may largely duplicate the educational 
benefits of a critical habitat designation. Including lands in critical 
habitat also informs State agencies and local governments about areas 
that could be conserved under State laws or local ordinances.

Conservation Partnerships on Non-Federal Lands

    Most federally listed species in the United States will not recover 
without cooperation of non-Federal landowners. More than 60 percent of 
the United States is privately owned (National Wilderness Institute 
1995), and at least 80 percent of endangered or threatened species 
occur either partially or solely on private lands (Crouse et al. 2002). 
Stein et al. (1995) found that only about 12 percent of listed species 
were found almost exclusively on Federal lands (90 to 100 percent of 
their known occurrences restricted to Federal lands) and that 50 
percent of federally listed species are not known to occur on Federal 
lands at all.
    Given the distribution of listed species with respect to land 
ownership, conservation of listed species in many parts of the United 
States is dependent upon working partnerships with a wide variety of 
entities and the voluntary cooperation of many non-Federal landowners 
(Wilcove and Chen 1998; Crouse et al. 2002; James 2002). Building 
partnerships and promoting voluntary cooperation of landowners are 
essential to understanding the status of species on non-Federal lands, 
and necessary for us to implement recovery actions such as 
reintroducing listed species, habitat restoration, and habitat 
protection.
    Many non-Federal landowners derive satisfaction from contributing 
to endangered species recovery. We promote these private-sector efforts 
through the Department of the Interior's Cooperative Conservation 
philosophy. Conservation agreements with non-Federal landowners (HCPs, 
safe harbor agreements, other conservation agreements, easements, and 
State and local regulations) enhance species conservation by extending 
species protections beyond those available through section 7 
consultations. In the past decade, we have encouraged non-Federal 
landowners to enter into conservation agreements, based on a view that 
we can achieve greater species conservation on non-Federal land through 
such partnerships than we can through regulatory methods (61 FR 63854; 
December 2, 1996).
    Many private landowners, however, are wary of the possible 
consequences of encouraging endangered species to their property, and 
there is mounting evidence that some regulatory actions by the Federal 
Government, while well-intentioned and required by law, can (under 
certain circumstances) have unintended negative consequences for the 
conservation of species on private lands (Wilcove et al. 1996; Bean 
2002; Conner and Mathews 2002; James 2002; Koch 2002; Brook et al. 
2003). Many landowners fear a decline in their property value due to 
real or perceived restrictions on land-use options where threatened or 
endangered species are found. Consequently, harboring endangered 
species is viewed by many landowners as a liability. This perception 
results in anti-conservation incentives because maintaining habitats 
that harbor endangered species represents a risk to future economic 
opportunities (Main et al. 1999; Brook et al. 2003).
    According to some researchers, the designation of critical habitat 
on private lands significantly reduces the likelihood that landowners 
will support and carry out conservation actions (Main et al. 1999; Bean 
2002; Brook et al. 2003). The magnitude of this negative outcome is 
greatly amplified in situations where active management measures (such 
as reintroduction, fire management, and control of invasive species) 
are necessary for species conservation (Bean 2002). We believe that the 
judicious exclusion of specific areas of non-federally owned lands from 
critical habitat designations can contribute to species recovery and 
provide a superior level of conservation than critical habitat alone.
    The purpose of designating critical habitat is to contribute to the 
conservation of threatened and endangered species and the ecosystems 
upon which they depend. The outcome of the designation, triggering 
regulatory requirements for actions funded, authorized, or carried out 
by Federal agencies under section 7(a)(2) of the Act, can sometimes be 
counterproductive to its intended purpose on non-Federal lands. Thus 
the benefits of excluding areas that are covered by partnerships or 
voluntary conservation efforts can often be high.

Benefits of Excluding Lands With Approved Management Plans

    The benefits of excluding lands with approved long-term management 
plans from critical habitat designation include relieving landowners, 
communities, and counties of any additional regulatory burden that 
might be imposed by critical habitat. Many conservation plans take 
years to develop, and upon completion, are consistent with recovery 
objectives for listed species that are covered within the plan area. 
Many also provide conservation benefits to unlisted sensitive species. 
Our experience in implementing the Act has found that designation of 
critical habitat within the boundaries of management plans that provide 
conservation measures for a species is a disincentive to many entities 
which are either currently developing such plans, or contemplating 
doing so in the future, because one of the incentives for undertaking 
conservation is greater ease of permitting where listed species will be 
affected. Addition of a new regulatory requirement would remove a 
significant incentive for undertaking the time and expense of 
management planning. In fact, designating critical habitat for species 
in areas covered by a conservation plan could result in the loss of 
some species' benefits if participants abandon the planning process in 
part because of the strength of the perceived additional regulatory 
compliance that such designation would entail. The time and cost of 
regulatory compliance for a critical habitat designation do not have to 
be quantified for them to be perceived as additional Federal regulatory 
burden sufficient to discourage continued participation in developing 
plans targeting listed species' conservation.
    A related benefit of excluding lands covered by approved management 
plans

[[Page 10373]]

from critical habitat designation is the unhindered, continued ability 
it gives us to seek new partnerships with future plan participants, 
including States, counties, local jurisdictions, conservation 
organizations, and private landowners, which together can implement 
conservation actions that we would be unable to accomplish otherwise. 
Designating lands within approved management plan areas as critical 
habitat would likely have a negative effect on our ability to establish 
new partnerships to develop these plans, particularly plans that 
address landscape-level conservation of plant species and habitats. By 
excluding these lands, we preserve our current partnerships and 
encourage additional conservation actions in the future.
    Furthermore, both HCPs and Natural Communities Conservation Plan 
(NCCP)-HCP applications require consultation, which would review the 
effects of all HCP-covered activities that might adversely impact the 
species under a jeopardy standard, including possibly significant 
habitat modification, even without the critical habitat designation. 
Additionally, all other Federal actions that may affect the listed 
species still require consultation under section 7(a)(2) of the Act, 
and we review these actions for possibly significant habitat 
modification in accordance with the jeopardy standard under section 7 
of the Act.

Exclusions Under Section 4(b)(2) of the Act

    We received several public comments suggesting we exclude lands 
enrolled under conservation agreements, through programs such as NRCS 
Conservation Reserve Program (CRP), Wildlife Habitat Improvement 
Program (WHIP), Environmental Quality Incentives Program (EQIP), 
Emergency Watershed Program (EWP), and the Service's Partners for Fish 
and Wildlife Program (PFW), from critical habitat designation. While we 
believe that excluding lands enrolled in those specific conservation 
agreements may provide benefits in terms of maintaining landowner 
cooperation, landowners who enroll in those programs are not bound by 
an easement that permanently prohibits development or conversion of 
those lands. Instead, landowners sign an agreement (generally 10 to 15 
years in duration) and at the end of that agreement those properties 
may be converted to another use. In those instances, the protection 
provided to those lands is not significantly different from that 
provided by a critical habitat designation under section 7 of the Act 
(i.e., adverse modification or destruction). As indicated in our 
response to Comment 24 in the ``Public Comments'' section above we do 
not conclude that the benefits of excluding those specific lands 
outweigh the benefits of including them in the designation. Therefore, 
they have not been excluded from this designation.
    However, after consideration under section 4(b)(2) of the Act, we 
are excluding approximately 50,298 ac (20,355 ha) of non-Federal lands 
in Units 1 and 2 enrolled under permanent/perpetual easements in the 
NRCS' WRP from the critical habitat designation for the Louisiana black 
bear.
    We excluded these areas because we believe that:
    (1) Their value for conservation will be preserved for the 
foreseeable future by existing protective actions; or
    (2) They are appropriate for exclusion under the ``other relevant 
impact'' provisions of section 4(b)(2) of the Act.
    In the paragraphs below, we provide a detailed analysis of our 
exclusion of these lands under section 4(b)(2) of the Act.
Permanent Easement Wetland Reserve Program Lands--Exclusions Under 
Section 4(b)(2) of the Act
    In reviewing lands enrolled under permanent easements under the WRP 
for potential exclusion under section 4(b)(2) of the Act, we consider 
(in addition to the general partnership relationships identified above) 
whether those easements provide for protection and appropriate 
management, if necessary, of essential habitat and whether the easement 
incorporates conservation management strategies and actions consistent 
with currently accepted principles of conservation biology.
    The WRP is a voluntary program that provides eligible landowners 
the opportunity to address wetland, wildlife habitat, soil, water, and 
related natural resource concerns on private lands in an 
environmentally beneficial and cost-effective manner. The WRP is 
authorized by 16 U.S.C. 3837 et seq., and the implementing regulations 
are found at 7 CFR part 1467. The first and foremost emphasis of the 
WRP is to protect, restore, and enhance the functions and values of 
wetland ecosystems to attain habitat for migratory birds and wetland-
dependent wildlife, including threatened and endangered species. The 
WRP is administered by the NRCS (in agreement with the Farm Service 
Agency) and in consultation with the Service and other cooperating 
agencies and organizations. The Service participates in several ways, 
including assisting NRCS with land eligibility determinations; 
providing the biological information for determining environmental 
benefits; assisting in restoration planning such that easement lands 
achieve maximum wildlife benefits and wetland values and functions; and 
providing recommendations regarding the timing, duration, and intensity 
of landowner-requested compatible uses.
    Land that is eligible for enrollment in the WRP includes such areas 
as wetlands cleared or drained for farming, pasture, or timber 
production; certain adjacent lands that contribute significantly to 
wetland functions and values; restored wetlands that need long-term 
protection; and existing or restorable riparian habitat corridors that 
connect protected wetlands. Eligible land must be restorable and 
suitable for providing wildlife benefits. Thus, the WRP provides an 
incentive for private landowners to restore non-productive farmland 
(prior-converted wetlands), and in Louisiana the majority of WRP land 
under permanent easement is agricultural land that is being restored to 
its original bottomland hardwood forest habitat.
    Under the WRP, there are three enrollment options available for the 
landowner: (1) Permanent/perpetual easement; (2) 30-year easement; and 
(3) restoration cost-share agreement. Under the permanent easement 
option, a conservation easement is placed upon the enrolled lands for 
perpetuity. When a landowner enrolls in an easement option, the 
landowner is selling a real property interest to the United States. 
After the easement is recorded in the local lands record office, the 
landowner retains ownership and responsibility for the land. The 
landowner controls access to the land; has the right to hunt, fish, and 
pursue other undeveloped recreational uses provided such use does not 
impact other prohibitions listed in the warranty easement deed; and may 
sell or lease land enrolled in the program (NRCS 2007; pp. 1-2).
    Participating landowners may request other prohibited uses such as 
haying, grazing, or harvesting timber. When evaluating compatible uses, 
the NRCS evaluates whether that proposed use is consistent with the 
long-term protection and enhancement of the wetland resources for which 
the easement was established and Federal funds expended. Requests may 
be approved if the NRCS determines that the activity both enhances and 
protects the purposes for which the easement was acquired and would not 
adversely affect habitat for migratory birds and threatened and 
endangered species.

[[Page 10374]]

NRCS retains the right to cancel an approved compatible use 
authorization at any time if it is deemed necessary to protect the 
functions and values of the easement. According to the authorizing 
language (16 U.S.C. 3837a(d)), compatible economic uses, including 
forest management, are permitted if consistent with the long-term 
protection and enhancement of the wetland resources for which the 
easement was established. Should such a modification be considered, 
NRCS would consult with the Service prior to making any changes.

Benefits of Inclusion--Permanent Easement Wetland Reserve Program Lands

    The inclusion of approximately 48,751 ac (19,729 ha) of land in 
Unit 1 and approximately 1,547 ac (626 ha) of land in Unit 2 enrolled 
in a permanent easement under the WRP could be beneficial because it 
identifies lands to be managed for the conservation and recovery of the 
Louisiana black bear. The process of proposing and finalizing a 
critical habitat provided the Service with the opportunity to determine 
the physical and biological features, or PCEs, essential for 
conservation of the species within the geographical area occupied by 
the species at the time of listing, as well as to determine if there 
were other areas essential to the conservation of the species. The 
designation process includes peer review and public comment on the 
identified features and areas. This process is valuable to land owners 
and managers in developing conservation management plans for identified 
areas, as well as any other occupied habitat or suitable habitat that 
may not have been included in the Service's determination of essential 
habitat. However, identification of important habitat for the Louisiana 
black bear and efforts to conserve the subspecies and its habitat were 
initiated in the early 1990s and resulted in the development of the 
``Louisiana Black Bear Habitat Restoration Planning Maps'' (HRPM). 
Those maps, developed by a collaborative multi-agency and organization 
group, were designed to directly address Louisiana black bear recovery 
criteria and designed for use with conservation programs (especially 
for the WRP), which encourage reforestation of marginal and 
nonproductive cropland in Louisiana.
    Permanent easements under the WRP provide substantial protection 
and management for the Louisiana black bear and its essential habitat 
features. In contrast, the only regulatory benefit to critical habitat 
designation is through the consultation provisions of section 7 of the 
Act, for Federal actions that may destroy or adversely modify critical 
habitat. Moreover, the educational benefits of designation are small 
and largely redundant to those derived through conservation efforts 
already in place or underway on the 48,751 ac (19,729 ha) of land in 
Unit 1 and the approximately 1,547 ac (626 ha) of land in Unit 2 that 
are protected under the WRP permanent easement. The process of 
developing the HRPM since 1992 has involved extensive input and the 
involvement of Federal, State, and local government partners including 
(but not limited to): NRCS, LDWF, BBCC, Louisiana State University, the 
Louisiana Nature Conservancy, and the Service. Therefore, the 
educational benefits of designating these private lands in Units 1 and 
2 as critical habitat are minimal.
    The consultation provisions under section 7(a) of the Act 
constitute the regulatory benefits of designating lands as critical 
habitat. As discussed above, Federal agencies must consult with us on 
actions that may affect critical habitat and must avoid destroying or 
adversely modifying critical habitat. However, for all of the 
approximately 50,298 ac (20,355 ha) of land in Units 1 and 2 under a 
WRP permanent easement, any changes to the easement would be approved 
only if the NRCS determines that the activity both enhances and 
protects the purposes for which the easement was acquired. Therefore, 
we do not anticipate a regulatory benefit to result from designation of 
those areas as critical habitat.

Benefits of Exclusion--Permanent Easement Wetland Reserve Program Lands

    In contrast to the lack of an appreciable benefit by including 
these lands as critical habitat, their exclusion from critical habitat 
will help preserve the partnerships that we have developed with the 
NRCS, other groups and agencies, and private landowners through the 
development and use of the HRPMs in the implementation of WRP permanent 
easements. At the time of listing, approximately one-half of Louisiana 
black bear breeding habitat was privately owned (BBCC 1997, p. 31), 
making the support and participation of private landowners vital to 
this subspecies' recovery. As discussed above, and evident in the 
public comments we received, many landowners perceive critical habitat 
as an unfair and unnecessary regulatory burden imposed on them for 
conducting an activity that benefits Louisiana black bear conservation 
measures such as enrolling in a WRP permanent easement. A significant 
amount of habitat restoration specifically designed to conserve and 
recover the Louisiana black bear has been accomplished through the use 
of the HRPMs and the voluntary cooperation of private landowners 
enrolled in the WRP.
    Since 1992, over 55,000 ac (22,250 ha) of private lands have been 
enrolled in the NRCS' WRP within critical habitat, which has benefited 
Louisiana black bear conservation. We have no quantitative data to 
prove that landowner enrollment in voluntary conservation programs may 
decrease as the result of critical habitat designation. We received 
unfavorable landowner responses during the 1993-94 critical habitat 
proposal process when the majority of comments received were in 
opposition to the designation, and several landowners who had 
previously allowed black bear research activities on their lands 
subsequently denied access to researchers and agency personnel. 
Furthermore, the NRCS' staff and managers, who work with private 
landowners on a daily basis, have indicated that there would likely be 
negative impacts (real or perceived) to voluntary conservation 
activities on private property by designating existing and newly 
created habitat as critical habitat and thus could result in a 
significant detrimental effect on future voluntary habitat restoration 
efforts (May 29, 2008, meeting with the Service). Similarly, comments 
from other professionals (Louisiana Department of Wildlife and 
Fisheries) and peer reviewers who interact regularly with private 
landowners, as well as comments received from a conservation group and 
landowners themselves, have indicated their belief that the negative 
perceptions associated with critical habitat designation would have 
detrimental impacts on black bear conservation efforts and enrollment 
in voluntary landowner conservation programs. In the case of lands 
enrolled under a permanent easement in the WRP, those easement 
restrictions provide substantial protection and management for the 
Louisiana black bear and its essential habitat features above that 
provided by designation of critical habitat, which only precludes 
destruction or adverse modification.
    Finally, landowner enrollment in the WRP has been primarily driven 
by the financial incentive provided to them through the easement 
payment and, in many instances, a desire to restore the land for 
Louisiana black bears or other wildlife. We know of no data that would 
indicate an increase in voluntary

[[Page 10375]]

landowner enrollment due to possible regulatory restrictions. On the 
contrary, the comments we have received during the comments period 
indicate the opposite.

Benefits of Exclusion Outweigh the Benefits of Inclusion--Permanent 
Easement Wetland Reserve Program Lands

    We reviewed and evaluated the benefits of inclusion and the 
benefits of exclusion of lands enrolled in permanent easement under the 
WRP as critical habitat for the Louisiana black bear. We found that the 
benefits of inclusion were minimal since protections afforded by the 
WRP permanent easements currently provide just as much, if not more, 
protection than critical habitat designation would provide. We also 
found substantial benefits to excluding these areas, such as 
maintaining non-Federal partnerships and providing opportunities for 
using flexible tools for restoration of the Louisiana black bear's 
habitat. We believe the cooperation of private landowners to provide 
access to habitat and participate in restoration actions would be lost 
if critical habitat were designated on these lands. Based on this 
evaluation, we find that the benefit of excluding lands enrolled in 
permanent easement under the WRP lands outweighs the benefit of 
including those lands as critical habitat for the Louisiana black bear.

Exclusion Will Not Result in Extinction of the Species--Permanent 
Easement Wetland Reserve Program Lands

    Exclusion of these 50,298 ac (20,355 ha) of non-Federal lands from 
the final designation of critical habitat will not result in the 
extinction of the Louisiana black bear because these lands are 
permanently conserved and are, or will be, managed for the benefit of 
this subspecies under the terms of the WRP permanent easement. The 
jeopardy standard of section 7 of the Act and routine implementation of 
habitat protection through the section 7 process also provide 
assurances that the subspecies will not go extinct. The protections 
afforded to the Louisiana black bear under the jeopardy standard will 
remain in place for the areas excluded from critical habitat.

Economic Analysis

    Section 4(b)(2) of the Act requires us to designate critical 
habitat on the basis of the best scientific information available and 
to consider the economic and other relevant impacts of designating a 
particular area as critical habitat. Section 4(b)(2) of the Act allows 
the Secretary to exclude areas from critical habitat for economic 
reasons if the Secretary determines that the benefits of such 
exclusions outweigh the benefits of designating the area as critical 
habitat. However, this exclusion cannot occur if it will result in the 
extinction of the species concerned.
    Following the publication of the proposed critical habitat 
designation, we conducted an economic analysis to estimate the 
potential economic effect of the designation. The draft economic 
analysis (DEA) was made available for public review on November 12, 
2008 (73 FR 66831). We accepted comments and information on the DEA 
until December 12, 2008. Following the close of the comment period, a 
final analysis of the potential economic effects of the designation 
(FEA) was developed taking into consideration the public comments and 
any new information.
    The primary purpose of the FEA is to estimate the potential 
economic impacts associated with the designation of critical habitat 
for the Louisiana black bear. This information is intended to assist 
the Secretary in making decisions about whether the benefits of 
excluding particular areas from the designation outweigh the benefits 
of including those areas in the designation. This economic analysis 
considers the economic efficiency effects that may result from the 
designation, including habitat protections that may be co-extensive 
with the listing of the species. The economic analysis separates the 
costs associated with conservation measures and economic impacts that 
occurred pre-designation from those that are likely to occur as a 
result of the designation. It also addresses distribution of impacts, 
including an assessment of the potential effects on small entities and 
the energy industry. The economic analysis separated the costs 
associated with the areas that we proposed to exclude from the areas 
that we proposed to designate at the time of the May 6, 2008, proposed 
rule (73 FR 25354). This information can be used by the Secretary to 
assess whether the effects of the designation might unduly burden a 
particular group or economic sector.
    The economic analysis focuses on the direct and indirect costs of 
the rule. However, economic impacts to land use activities can exist in 
the absence of critical habitat. These impacts may result from, for 
example, local zoning laws, State and natural resource laws, and 
enforceable management plans and best management practices applied by 
other State and Federal agencies. Economic impacts that result from 
these types of protections are not included in the analysis as they are 
considered to be part of the regulatory and policy baseline.
    The economic analysis examines activities taking place both within 
and adjacent to the designation. It estimates impacts based on 
activities that are ``reasonably foreseeable'' including, but not 
limited to, activities that are currently authorized, permitted, or 
funded, or for which proposed plans are currently available to the 
public. Accordingly, the analysis bases estimates on activities that 
are likely to occur within a 20-year timeframe from when the proposed 
rule became available to the public (73 FR 25354; May 6, 2008). The 20-
year timeframe was chosen for the analysis because, as the time horizon 
for an economic analysis is expanded, the assumptions on which the 
projected number of projects and cost impacts associated with those 
projects become increasingly speculative.
    Based on our analysis, we concluded that the designation of 
critical habitat would not result in a significant economic impact. The 
present estimated value of baseline economic impacts associated with 
Louisiana black bear conservation efforts ranged from $68.4 million to 
$76.6 million discounted at 3 percent, or $84.9 million to $97 million 
discounted at 7 percent. The potential post-designation incremental 
economic impacts for the next 20 years range from $1.5 million to $8.6 
million, applying a 3 percent discount rate, or $1.1 million to $6.3 
million applying a 7 percent discount rate. The range in values of 
incremental costs is a result of the uncertainty in forecasting the 
number of new oil and gas wells that are likely to be drilled in the 
next 20 years.
    Economic impacts attributable to critical habitat designation 
(i.e., incremental impacts) are associated entirely with oil and gas 
activities. Incremental costs were based on industry costs associated 
with the modification or relocation of above-ground well sites.
    The post-designation baseline costs for the WRP were estimated to 
be $6.2 million based on the assumption that WRP enrollment would 
continue at the same rate as the past over the next 20 years. There may 
be an incremental effect of decreased WRP enrollment as a result of 
critical habitat designation for the Louisiana black bear; however 
there was insufficient public data to quantify that anticipated 
decrease.
    We do not find the economic costs to be significant. Therefore, we 
have not excluded any areas from this designation of critical habitat 
based on economic impacts.

[[Page 10376]]

    A copy of the FEA (with supporting documents) is included in our 
supporting file and may be obtained by contacting Lafayette Ecological 
Services Field Office (see ADDRESSES section) or for downloading from 
the Internet at http://www.regulations.gov or http://www.fws.gov/lafayette.

Required Determinations

Regulatory Planning and Review

    The Office of Management and Budget (OMB) has determined that this 
rule is not significant and has not reviewed this rule under Executive 
Order 12866 (E.O. 12866). OMB bases its determination upon the 
following four criteria:
    (a) Whether the rule will have an annual effect of $100 million or 
more on the economy or adversely affect an economic sector, 
productivity, jobs, the environment, or other units of the government.
    (b) Whether the rule will create inconsistencies with other Federal 
agencies' actions.
    (c) Whether the rule will materially affect entitlements, grants, 
user fees, loan programs or the rights and obligations of their 
recipients.
    (d) Whether the rule raises novel legal or policy issues.

Regulatory Flexibility Act (5 U.S.C. 601 et seq.)

    Under the Regulatory Flexibility Act (RFA; 5 U.S.C. 601 et seq.), 
as amended by the Small Business Regulatory Enforcement Fairness Act 
(SBREFA), whenever an agency must publish a notice of rulemaking for 
any proposed or final rule, it must prepare and make available for 
public comment a regulatory flexibility analysis that describes the 
effect of the rule on small entities (i.e., small businesses, small 
organizations, and small government jurisdictions). However, no 
regulatory flexibility analysis is required if the head of an agency 
certifies the rule will not have a significant economic impact on a 
substantial number of small entities. SBREFA amended RFA to require 
Federal agencies to provide a certification statement of factual basis 
for certifying that the rule will not have a significant economic 
impact on a substantial number of small entities. In this final rule, 
we are certifying that the critical habitat designation for the 
Louisiana black bear will not have a significant economic impact on a 
substantial number of small entities. The following discussion explains 
our rationale.
    According to the Small Business Administration (SBA), small 
entities include small organizations, such as independent nonprofit 
organizations; small governmental jurisdictions, including school 
boards and city and town governments that serve fewer than 50,000 
residents; as well as small businesses. Small businesses include 
manufacturing and mining concerns with fewer than 500 employees, 
wholesale trade entities with fewer than 100 employees, retail and 
service businesses with less than $5 million in annual sales, general 
and heavy construction businesses with less than $27.5 million in 
annual business, special trade contractors doing less than $11.5 
million in annual business, and agricultural businesses with annual 
sales less than $750,000. To determine if potential economic impacts to 
these small entities are significant, we consider the types of 
activities that might trigger regulatory impacts under this rule, as 
well as the types of project modifications that may result. In general, 
the term ``significant economic impact'' is meant to apply to a typical 
small business firm's business operations.
    To determine if the rule could significantly affect a substantial 
number of small entities, we consider the number of small entities 
affected within particular types of economic activities (e.g., housing 
development, grazing, oil and gas production, timber harvesting). We 
apply the ``substantial number'' test individually to each industry to 
determine if certification is appropriate. However, the SBREFA does not 
explicitly define ``substantial number'' or ``significant economic 
impact.'' Consequently, to assess whether a ``substantial number'' of 
small entities is affected by this designation, this analysis considers 
the relative number of small entities likely to be impacted in an area. 
In some circumstances, especially with critical habitat designations of 
limited extent, we may aggregate across all industries and consider 
whether the total number of small entities affected is substantial. In 
estimating the number of small entities potentially affected, we also 
consider whether their activities have any Federal involvement.
    Designation of critical habitat only affects activities authorized, 
funded, or carried out by Federal agencies. Some kinds of activities 
are unlikely to have any Federal involvement and so will not be 
affected by critical habitat designation. In areas where the subspecies 
is present, Federal agencies already are required to consult with us 
under section 7 of the Act on activities they authorize, fund, or carry 
out that may affect the Louisiana black bear. Federal agencies also 
must consult with us if their activities may affect critical habitat. 
Designation of critical habitat, therefore, could result in an 
additional economic impact on small entities due to the requirement to 
reinitiate consultation for ongoing Federal activities (see Application 
of the ``Adverse Modification Standard'' section).
    In our final economic analysis of the proposed critical habitat 
designation, we evaluated the potential economic effects on small 
business entities resulting from conservation actions related to the 
listing of the Louisiana black bear and the proposed designation of 
critical habitat. The analysis is based on the estimated impacts 
associated with the proposed rulemaking as described in Chapters 2 
through 7 and Appendix A of the analysis and evaluates the potential 
for economic impacts related to: (1) Oil and gas exploration and 
development; (2) subspecies/habitat management; (3) recreational and 
residential development; (4) agriculture; (5) transportation; and (6) 
forestry.
    The final economic analysis identified 45 small entities that may 
be affected by the designation of critical habitat for the Louisiana 
black bear. All of those entities were associated with oil and gas 
development and exploration. The total estimated impact per small 
entity over 20 years would range from between 1.0 to 5.4 percent of the 
small entity's median revenues. Additionally, the final economic 
analysis estimates annualized impacts associated with conservation 
activities for the Louisiana black bear could range from $25,100 to 
$141,000 discounted at the 7 percent rate over the next 20 years.
    The final economic analysis concludes that, with the exception of 
impacts related to oil and gas exploration and development, there are 
no incremental impacts resulting from designation of critical habitat 
for the Louisiana black bear that may be borne by small businesses.
    In summary, we considered whether this designation would result in 
a significant economic effect on a substantial number of small 
entities. Based on the above reasoning and currently available 
information, we concluded that this rule would not result in a 
significant economic impact on a substantial number of small entities. 
Therefore, we are certifying that the designation of critical habitat 
for the Louisiana black bear will not have a significant economic 
impact on a substantial number of small entities, and a regulatory 
flexibility analysis is not required.

[[Page 10377]]

Small Business Regulatory Enforcement Fairness Act (5 U.S.C 801 et 
seq.)

    Under SBREFA, this rule is not a major rule. Our detailed 
assessment of the economic effects of this designation is described in 
the final economic analysis. Based on the effects identified in the 
economic analysis, we believe that this rule will not have an annual 
effect on the economy of $100 million or more, will not cause a major 
increase in costs or prices for consumers, and will not have 
significant adverse effects on competition, employment, investment, 
productivity, innovation, or the ability of U.S.-based enterprises to 
compete with foreign-based enterprises. Refer to the final economic 
analysis for a discussion of the effects of this determination.

Executive Order 13211

    On May 18, 2001, the President issued Executive Order 13211 (E.O. 
13211; ``Actions Concerning Regulations That Significantly Affect 
Energy Supply, Distribution, or Use'') on regulations that 
significantly affect energy supply, distribution, and use. E.O. 13211 
requires agencies to prepare Statements of Energy Effects when 
undertaking certain actions. OMB has provided guidance for implementing 
this Executive Order that outlines nine outcomes that may constitute 
``a significant adverse effect'' when compared to not taking the 
regulatory action under consideration. The economic analysis finds that 
none of these criteria are relevant to this analysis. Thus, based on 
information in the economic analysis, energy-related impacts associated 
with Louisiana black bear conservation activities within critical 
habitat are not expected. As such, the designation of critical habitat 
is not expected to significantly affect energy supplies, distribution, 
or use. Therefore, this action is not a significant energy action, and 
no Statement of Energy Effects is required.

Unfunded Mandates Reform Act (2 U.S.C. 1501 et seq.)

    In accordance with the Unfunded Mandates Reform Act (2 U.S.C. 1501 
et seq.), we make the following findings:
    (a) This rule will not produce a Federal mandate. In general, a 
Federal mandate is a provision in legislation, statute, or regulation 
that would impose an enforceable duty upon State, local, or Tribal 
governments, or the private sector, and includes both ``Federal 
intergovernmental mandates'' and ``Federal private sector mandates.'' 
These terms are defined in 2 U.S.C. 658(5)-(7). ``Federal 
intergovernmental mandate'' includes a regulation that ``would impose 
an enforceable duty upon State, local, or tribal governments'' with two 
exceptions. It excludes ``a condition of Federal assistance.'' It also 
excludes ``a duty arising from participation in a voluntary Federal 
program,'' unless the regulation ``relates to a then-existing Federal 
program under which $500,000,000 or more is provided annually to State, 
local, and tribal governments under entitlement authority,'' if the 
provision would ``increase the stringency of conditions of assistance'' 
or ``place caps upon, or otherwise decrease, the Federal Government's 
responsibility to provide funding,'' and the State, local, or Tribal 
governments ``lack authority'' to adjust accordingly. At the time of 
enactment, these entitlement programs were: Medicaid; Aid to Families 
with Dependent Children work programs; Child Nutrition; Food Stamps; 
Social Services Block Grants; Vocational Rehabilitation State Grants; 
Foster Care, Adoption Assistance, and Independent Living; Family 
Support Welfare Services; and Child Support Enforcement. ``Federal 
private sector mandate'' includes a regulation that ``would impose an 
enforceable duty upon the private sector, except (i) a condition of 
Federal assistance or (ii) a duty arising from participation in a 
voluntary Federal program.''
    The designation of critical habitat does not impose a legally 
binding duty on non-Federal Government entities or private parties. 
Under the Act, the only regulatory effect is that Federal agencies must 
ensure that their actions do not result in the destruction or adverse 
modification of critical habitat. Non-Federal entities that receive 
Federal funding, assistance, or permits, or that otherwise require 
approval or authorization from a Federal agency for an action, may be 
indirectly impacted by the designation of critical habitat. However, 
the legally binding duty to avoid destruction or adverse modification 
of critical habitat rests squarely on the Federal agency. Furthermore, 
to the extent that non-Federal entities are indirectly impacted because 
they receive Federal assistance or participate in a voluntary Federal 
aid program, the Unfunded Mandates Reform Act would not apply, nor 
would critical habitat shift the costs of the large entitlement 
programs listed above onto State governments.
    (b) We do not believe that this rule will significantly or uniquely 
affect small governments because it will not produce a Federal mandate 
of $100 million or greater in any year, that is, it is not a 
``significant regulatory action'' under the Unfunded Mandates Reform 
Act. The designation of critical habitat imposes no obligations on 
State or local governments. By definition, Federal agencies are not 
considered small entities, although the activities they fund or permit 
may be proposed or carried out by small entities. As such, a Small 
Government Agency Plan is not required.

Executive Order 12630--Takings

    In accordance with E.O. 12630 (``Government Actions and 
Interference with Constitutionally Protected Private Property 
Rights''), we have analyzed the potential takings implications of 
designating critical habitat for the Louisiana black bear in a takings 
implications assessment. Critical habitat designation does not affect 
landowner actions that do not require Federal funding or permits, nor 
does it preclude development of habitat conservation programs or 
issuance of incidental take permits to permit actions that do require 
Federal funding or permits to go forward. The takings implications 
assessment concludes that this designation of critical habitat for the 
Louisiana black bear does not pose significant takings implications for 
lands within or affected by the designation.

Federalism

    In accordance with E.O. 13132 (Federalism), this rule does not have 
significant Federalism effects. A Federalism assessment is not 
required. In keeping with Department of the Interior and Department of 
Commerce policy, we requested information from, and coordinated 
development of, this critical habitat designation with appropriate 
State resource agencies in Louisiana. We received comments from the 
Louisiana Department of Wildlife and Fisheries and the Louisiana 
Department of Natural Resources and have addressed them in the Response 
to Comments section of the rule. The designation of critical habitat in 
areas currently occupied by the Louisiana black bear may impose nominal 
additional regulatory restrictions to those currently in place and, 
therefore, may have little incremental impact on State and local 
governments and their activities. The designation may have some benefit 
to these governments in that the areas that contain the physical and 
biological features essential to the conservation of the subspecies are 
more clearly defined, and the PCEs of the habitat necessary to the 
conservation of the subspecies are specifically identified. This 
information does not alter where and what federally

[[Page 10378]]

sponsored activities may occur. However, it may assist local 
governments in long-range planning (rather than having them wait for 
case-by-case section 7 consultations to occur).

Civil Justice Reform

    In accordance with E.O. 12988 (Civil Justice Reform), the 
regulation meets the applicable standards set forth in sections 3(a) 
and 3(b)(2) of the Order. We are designating critical habitat in 
accordance with the provisions of the Act. This final rule uses 
standard property descriptions and identifies the physical and 
biological features essential to the conservation of the subspecies 
within the designated areas to assist the public in understanding the 
habitat needs of the Louisiana black bear.

Paperwork Reduction Act of 1995

    This rule does not contain any new collections of information that 
require approval by OMB under the Paperwork Reduction Act of 1995 (44 
U.S.C. 3501 et seq.). This rule will not impose recordkeeping or 
reporting requirements on State or local governments, individuals, 
businesses, or organizations. An agency may not conduct or sponsor, and 
a person is not required to respond to, a collection of information 
unless it displays a currently valid OMB control number.

National Environmental Policy Act (NEPA)

    It is our position that, outside the Jurisdiction of the U.S. Court 
of Appeals for the Tenth Circuit, we do not need to prepare 
environmental analyses as defined by the NEPA (42 U.S.C. 4321 et seq.) 
in connection with designating critical habitat under the Act. We 
published a notice outlining our reasons for this determination in the 
Federal Register on October 25, 1983 (48 FR 49244). This position was 
upheld by the U.S. Court of Appeals for the Ninth Circuit (Douglas 
County v. Babbitt, 48 F.3d 1495 (9th Cir. 1995), cert. denied 516 U.S. 
1042 (1996)).

Government-to-Government Relationship With Tribes

    In accordance with the President's memorandum of April 29, 1994, 
``Government-to-Government Relations with Native American Tribal 
Governments'' (59 FR 22951), E.O. 13175, and the Department of the 
Interior's manual at 512 DM 2, we readily acknowledge our 
responsibility to communicate meaningfully with recognized Federal 
Tribes on a government-to-government basis. In accordance with 
Secretarial Order 3206 of June 5, 1997, ``American Indian Tribal 
Rights, Federal-Tribal Trust Responsibilities, and the Endangered 
Species Act,'' we readily acknowledge our responsibilities to work 
directly with Tribes in developing programs for healthy ecosystems, to 
acknowledge that Tribal lands are not subject to the same controls as 
Federal public lands, to remain sensitive to Indian culture, and to 
make information available to Tribes. We determined that there are no 
Tribal lands occupied at the time of listing that contain the features 
essential for the conservation, and no unoccupied Tribal lands that are 
essential for the conservation of the Louisiana black bear. Therefore, 
we are not designating critical habitat for the Louisiana black bear on 
Tribal lands.

References Cited

    A complete list of all references cited in this rulemaking is 
available upon request from the Field Supervisor, Lafayette Ecological 
Services Field Office (see ADDRESSES section).

Author(s)

    The primary authors of this rulemaking are the staff members of the 
Lafayette Ecological Services Field Office.

List of Subjects in 50 CFR Part 17

    Endangered and threatened species, Exports, Imports, Reporting and 
recordkeeping requirements, Transportation.

Regulation Promulgation

0
Accordingly, we amend part 17, subchapter B of chapter I, title 50 of 
the Code of Federal Regulations, as set forth below:

PART 17--[AMENDED]

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

    Authority: 16 U.S.C. 1361-1407; 16 U.S.C. 1531-1544; 16 U.S.C. 
4201-4245; Pub. L. 99-625, 100 Stat. 3500; unless otherwise noted.


0
2. Amend Sec.  17.11(h) by revising the entry for ``Bear, Louisiana 
black'' under ``MAMMALS'' in the List of Endangered and Threatened 
Wildlife to read as follows:


Sec.  17.11   Endangered and threatened wildlife.

* * * * *
    (h) * * *

--------------------------------------------------------------------------------------------------------------------------------------------------------
                        Species                                                      Vertebrate
--------------------------------------------------------                             population
                                                              Historic range            where          Status      When listed    Critical     Special
           Common name                Scientific name                               endangered or                                 habitat       rules
                                                                                     threatened
--------------------------------------------------------------------------------------------------------------------------------------------------------
             Mammals
 
                                                                      * * * * * * *
Bear, Louisiana black............  Ursus americanus      U.S.A. (LA--all           Entire........  T                       456     17.95(a)     17.40(i)
                                    luteolus.             counties; MS--all
                                                          counties south of or
                                                          touching a line from
                                                          Greenville, Washington
                                                          County, to Meridian,
                                                          Lauderdale County; TX--
                                                          all counties east of or
                                                          touching a line from
                                                          Linden, Cass County, SW
                                                          to Bryan, Brazos
                                                          County, thence SSW to
                                                          Rockport, Aransas
                                                          County).
 
                                                                      * * * * * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------


0
3. In Sec.  17.95, amend paragraph (a) by adding an entry for Louisiana 
Black Bear (Ursus americanus luteolus), in the same order that the 
subspecies appears in the table at Sec.  17.11(h), to read as follows:

[[Page 10379]]

Sec.  17.95   Critical habitat--fish and wildlife.

    (a) Mammals.
* * * * *
    Louisiana Black Bear (Ursus americanus luteolus)
    (1) Critical habitat units are depicted for Avoyelles, East 
Carroll, Catahoula, Concordia, Franklin, Iberia, Iberville, Madison, 
Pointe Coupee, Richland, St. Martin, St. Mary, Tensas, West Carroll, 
and West Feliciana Parishes, Louisiana, on the maps below.
    (2) The primary constituent elements of critical habitat for the 
Louisiana black bear are the habitat components that provide:
    (i) Breeding habitat (i.e., within or contiguous to the home range 
of females in a core breeding population) consisting of hardwood forest 
areas having a diversity of age class and species and containing 
sources of hard mast (acorns and nuts) produced by such species as 
mature oaks, hickories, and pecan, and that may include one or more of 
the following:
    (A) Areas containing soft mast provided by a diversity of plant 
species, including, but not limited to, blackberry, grape, mulberry, 
sassafras, paw paw, etc., occurring primarily in forest openings, on 
spoil banks, and in areas adjacent to forested habitat.
    (B) Areas within forested habitat providing protein sources 
consisting of beetles and other colonial insects found in rotting and 
decaying wood found on the forest floor.
    (C) Grasses and sedges found in forest openings, on spoil banks 
with open canopies, and in vegetated areas adjacent to forested 
habitats.
    (D) Secure areas for reproduction, winter dormancy, day bedding, 
and escape. These include areas with den trees (e.g., bald cypress, 
overcup oak, American sycamore, etc.); areas with a thick understory, 
shrub-scrub habitat, openings along spoil banks, vegetated areas 
adjacent to forests, or any vegetation that provides cover, limits 
visibility, slows foot travel, or creates noise when traversed; early 
successional forests (0 to 12 years) with an open canopy and dense 
understory of shrubs, vines, and saplings; or areas with vegetation 
such as palmetto, greenbriars, blackberry, dewberry, and downed trees.
    (ii) Corridors consisting of:
    (A) Habitat patches 12 acres (5 hectares) or greater in size; or
    (B) Forested areas greater than 150 feet (46 meters) wide along 
waterways and sloughs and having a diversity of plant species and age-
classes of sufficient area, quality, and configuration, as described in 
paragraph (2)(i) of this entry, to provide dispersal habitat between 
breeding populations to maintain genetic variability and promote stable 
or increasing populations, and to provide habitat supporting safe 
movement, foraging, and denning.
    (3) Critical habitat does not include manmade structures (such as 
buildings, aqueducts, runways, roads, and other paved areas) and the 
land on which they are located existing within the legal boundaries on 
the effective date of this rule.
    (4) Critical habitat map units. Data layers defining map units were 
created on a base of USGS digital ortho-photo quarter-quadrangles, and 
critical habitat units were then mapped using Universal Transverse 
Mercator (UTM) Zone 15N coordinates.
    (5) Note: Index map follows:
BILLING CODE 4310-55-P

[[Page 10380]]

[GRAPHIC] [TIFF OMITTED] TR10MR09.000

BILLING CODE 4310-55-C

[[Page 10381]]

    (6) Unit 1: Tensas River Basin. Avoyelles, East Carroll, Catahoula, 
Concordia, Franklin, Madison, Richland, Tensas, West Carroll, and West 
Feliciana Parishes, Louisiana.
    (i) From USGS 1:24,000 scale digital ortho-photo quarter-
quadrangles: Acme SE; Acme SW; Big Bend NE; Big Bend NW; Big Bend SE; 
Big Bend SW; Como NE; Como SE; Crowville NE; Crowville SE; Deer Park 
NW; Deer Park SW; Delhi NE; Delhi NW; Delhi SE; Delhi SW; Dunbarton NE; 
Dunbarton NW; Dunbarton SE; Dunbarton SW; Epps NE; Epps NW; Epps SE; 
Epps SW; Fairview NW; Fairview SW; Ferriday North NE; Ferriday North 
NW; Ferriday South NW; Ferriday South SW; Fort Adams NW; Fort Adams SE; 
Fort Adams SW; Fortune Fork NW; Fortune Fork SW; Foules NE; Foules NW; 
Foules SE; Foules SW; Frogmore NE; Frogmore NW; Frogmore SE; Frogmore 
SW; Gretna Green NE; Gretna Green NW; Gretna Green SE; Gretna Green SW; 
Ile Natchitoches NE; Ile Natchitoches NW; Ile Natchitoches SE; Ile 
Natchitoches SW; Indian Lake NE; Indian Lake NW; Indian Lake SE; Indian 
Lake SW; Innis NE; Lac Sainte Agnes NE; Lac Sainte Agnes NW; Lac Sainte 
Agnes SE; Lake Bruin NW; Lake Mary NW; Lake Mary SW; Lamar SE; Larto 
Lake South SE; Larto Lake South SW; Lower Sunk Lake NE; Lower Sunk Lake 
NW; Lower Sunk Lake SE; Lower Sunk Lake SW; Monterry NE; Monterry SE; 
Newlight NE; Newlight NW; Newlight SE; Newlight SW; Oakley NE; Oakley 
SE; Oakley SW; Panther Lake NE; Panther Lake NW; Panther Lake SE; 
Panther Lake SW; Saranac NW; Saranac SW; Simmesport NE; Simmesport NW; 
Slocum NE; Slocum NW; Slocum SE; Slocum SW; Somerset NW; Tallulah SW; 
Tendale NE; Tendal NW; Tendal SE; Tendal SW; Tensas Bluff NE; Tensas 
Bluff NW; Tensas Bluff SE; Tensas Bluff SW; Turnbull Island NE; 
Turnbull Island NW; Turnbull Island SE; Turnbull Island SW; Waterproof 
NE; Waterproof NW; Waterproof SE; Waterproof SW; Waverly SE NE; Waverly 
SE NW; Waverly SE SE; Waverly SE SW; Westwood NE; Westwood NW; Westwood 
SE; Westwood SW; Louisiana. Land bounded by the following UTM Zone 15N, 
North American Datum of 1983 (NAD83) coordinates (E, N): 627070, 
3431218; 618220, 3431485; 614348, 3433932; 615247, 3438430; 612584, 
3440854; 626123, 3431776; 617768, 3431231; 614471, 3434089; 615216, 
3438464; 612531, 3440860; 625650, 3432072; 617606, 3431085; 614560, 
3434183; 615191, 3438488; 612475, 3440863; 625406, 3432226; 617426, 
3430847; 614625, 3434252; 615151, 3438562; 612410, 3440872; 625184, 
3432321; 617241, 3430530; 614683, 3434324; 615091, 3438681; 612322, 
3440881; 624930, 3432387; 617093, 3430154; 614710, 3434353; 615039, 
3438779; 612255, 3440892; 624737, 3432448; 616955, 3429720; 614780, 
3434476; 615006, 3438858; 612193, 3440905; 624411, 3432472; 616887, 
3429397; 614844, 3434624; 614974, 3438974; 612159, 3440910; 624152, 
3432456; 616741, 3429104; 614916, 3434774; 614954, 3439032; 612123, 
3440914; 623962, 3432377; 616551, 3428866; 614963, 3434868; 614934, 
3439113; 612070, 3440914; 623811, 3432300; 616315, 3428667; 615037, 
3435015; 614889, 3439374; 612016, 3440919; 623692, 3432226; 616016, 
3428582; 615093, 3435134; 614835, 3439654; 611868, 3440941; 623602, 
3432109; 615619, 3428516; 615142, 3435253; 614813, 3439755; 611779, 
3440952; 623530, 3431990; 615339, 3428453; 615180, 3435338; 614789, 
3439831; 611712, 3440966; 623446, 3431757; 615011, 3428360; 615209, 
3435425; 614773, 3439862; 611571, 3440990; 623419, 3431670; 614759, 
3428249; 615249, 3435523; 614739, 3439918; 611450, 3441008; 623334, 
3431437; 614704, 3428322; 615319, 3435745; 614708, 3439959; 611383, 
3441013; 623255, 3431289; 614560, 3428511; 615408, 3436020; 614668, 
3440008; 611295, 3441024; 623065, 3431117; 614517, 3428564; 615464, 
3436235; 614614, 3440064; 611239, 3441033; 622948, 3431070; 614473, 
3428601; 615487, 3436304; 614504, 3440149; 611170, 3441028; 622678, 
3431022; 614412, 3428635; 615500, 3436354; 614417, 3440211; 611094, 
3441028; 622385, 3430980; 614354, 3428664; 615538, 3436456; 614363, 
3440254; 610984, 3441026; 622260, 3430982; 614241, 3428701; 615574, 
3436559; 614227, 3440348; 610893, 3441028; 622094, 3431032; 614176, 
3428719; 615585, 3436627; 614135, 3440406; 610787, 3441030; 621887, 
3431099; 614107, 3428730; 615587, 3436707; 614025, 3440460; 610608, 
3441042; 621760, 3431186; 614107, 3428782; 615581, 3436841; 613927, 
3440496; 610532, 3441048; 621631, 3431265; 614113, 3428816; 615569, 
3436913; 613860, 3440527; 610402, 3441053; 621453, 3431395; 614113, 
3428816; 615554, 3436978; 613761, 3440556; 610266, 3441055; 621313, 
3431493; 614109, 3429208; 615547, 3437034; 613685, 3440583; 610009, 
3441066; 621041, 3431681; 614106, 3429555; 615538, 3437211; 613605, 
3440610; 609924, 3441071; 620787, 3431845; 612461, 3429548; 615529, 
3437352; 613432, 3440675; 609836, 3441084; 620535, 3431940; 612453, 
3431630; 615529, 3437392; 613372, 3440690; 609619, 3441095; 620265, 
3432041; 612437, 3432776; 615540, 3437434; 613336, 3440699; 609519, 
3441102; 620181, 3432104; 614028, 3432781; 615556, 3437468; 613267, 
3440710; 609362, 3441109; 620101, 3432210; 614039, 3432872; 615540, 
3437524; 613193, 3440726; 609255, 3441115; 620040, 3432284; 614061, 
3433084; 615525, 3437631; 613117, 3440740; 609199, 3441118; 619964, 
3432342; 614070, 3433250; 615518, 3437712; 613059, 3440748; 609120, 
3441122; 619863, 3432366; 614066, 3433377; 615509, 3437763; 612987, 
3440769; 609073, 3441129; 619771, 3432387; 614055, 3433494; 615489, 
3437844; 612918, 3440784; 609013, 3441140; 619651, 3432384; 614048, 
3433637; 615467, 3437947; 612860, 3440793; 608968, 3441140; 619548, 
3432382; 614043, 3433702; 615435, 3438032; 612792, 3440809; 608905, 
3441149; 619429, 3432265; 614055, 3433711; 615390, 3438139; 612750, 
3440820; 608847, 3441158; 619265, 3432093; 614135, 3433755; 615319, 
3438267; 612687, 3440834; 608789, 3441167; 618937, 3431821; 614231, 
3433836; 615265, 3438379; 612631, 3440840; 608738, 3441176; 608662, 
3441189; 609199, 3442359; 610214, 3445121; 611238, 3446431; 610214, 
3445502; 608592, 3441198; 609224, 3442381; 610231, 3445174; 611279, 
3446480; 610173, 3445521; 608529, 3441209; 609253, 3442414; 610239, 
3445189; 611320, 3446544; 610132, 3445529; 608487, 3441218; 609275, 
3442441; 610263, 3445215; 611291, 3446558; 610077, 3445529; 608467, 
3441250; 609285, 3442476; 610292, 3445238; 611264, 3446575; 610050, 
3445527; 608447, 3441270; 609300, 3442506; 610319, 3445254; 611233, 
3446577; 610020, 3445496; 608429, 3441277; 609320, 3442570; 610382, 
3445289; 611197, 3446571; 609981, 3445465; 608397, 3441290; 609333, 
3442593; 610428, 3445310; 611166, 3446563; 609950, 3445435; 608366, 
3441308; 609347, 3442607; 610471, 3445326; 611131, 3446542; 609925, 
3445412; 608350, 3441326; 609374, 3442642; 610520, 3445344; 611106, 
3446511; 609884, 3445383; 608344, 3441355; 609400, 3442664; 610567, 
3445357; 611080, 3446472; 609825, 3445330; 608337, 3441487; 609435, 
3442705; 610598, 3445369; 611051, 3446435; 609757, 3445287; 608328, 
3441617; 609456, 3442759; 610624, 3445385; 611041, 3446405; 609691, 
3445252; 608333, 3441639; 609466, 3442837; 610647, 3445408; 611022,

[[Page 10382]]

3446349; 609650, 3445221; 608348, 3441664; 609474, 3442941; 610665, 
3445443; 611006, 3446316; 609589, 3445185; 608364, 3441697; 609470, 
3443011; 610674, 3445476; 610981, 3446261; 609531, 3445152; 608362, 
3441717; 609478, 3443060; 610696, 3445515; 610963, 3446218; 609490, 
3445131; 608355, 3441755; 609486, 3443101; 610704, 3445541; 610959, 
3446181; 609441, 3445125; 608341, 3441927; 609486, 3443148; 610713, 
3445566; 610936, 3446134; 609390, 3445119; 608336, 3441975; 609493, 
3443187; 610731, 3445591; 610930, 3446093; 609347, 3445133; 608334, 
3442025; 609499, 3443236; 610741, 3445609; 610918, 3446050; 609331, 
3445154; 608336, 3442056; 609493, 3443312; 610762, 3445625; 610909, 
3446027; 609314, 3445191; 608339, 3442060; 609482, 3443409; 610791, 
3445640; 610907, 3445997; 609296, 3445223; 608339, 3442060; 609466, 
3443497; 610811, 3445650; 610885, 3445953; 609275, 3445275; 608347, 
3442077; 609458, 3443554; 610846, 3445664; 610873, 3445923; 609263, 
3445303; 608423, 3442165; 609449, 3443647; 610879, 3445677; 610844, 
3445894; 609242, 3445359; 608461, 3442211; 609443, 3443694; 610899, 
3445707; 610813, 3445839; 609210, 3445416; 608485, 3442226; 609447, 
3443741; 610940, 3445759; 610731, 3445728; 609191, 3445451; 608511, 
3442233; 609454, 3443776; 610961, 3445810; 610702, 3445693; 609142, 
3445494; 608533, 3442238; 609472, 3443827; 610969, 3445857; 610665, 
3445660; 609099, 3445533; 608572, 3442239; 609488, 3443870; 610977, 
3445917; 610624, 3445644; 609062, 3445562; 608629, 3442241; 609501, 
3443915; 610981, 3445960; 610583, 3445615; 609037, 3445586; 608666, 
3442244; 609525, 3443956; 610987, 3446007; 610547, 3445588; 608990, 
3445593; 608715, 3442250; 609548, 3443995; 610998, 3446040; 610536, 
3445568; 608922, 3445607; 608793, 3442256; 609583, 3444048; 611002, 
3446062; 610514, 3445529; 608883, 3445603; 608840, 3442271; 609613, 
3444096; 611028, 3446107; 610499, 3445490; 608824, 3445611; 608894, 
3442297; 609642, 3444147; 611043, 3446154; 610489, 3445459; 608764, 
3445619; 608947, 3442324; 609681, 3444202; 611069, 3446197; 610471, 
3445422; 608709, 3445632; 608976, 3442340; 609710, 3444235; 611100, 
3446230; 610432, 3445398; 608660, 3445642; 609009, 3442347; 609747, 
3444266; 611131, 3446278; 610387, 3445390; 608609, 3445656; 609039, 
3442347; 609763, 3444284; 611151, 3446314; 610352, 3445392; 608541, 
3445671; 609082, 3442347; 609819, 3444391; 611172, 3446355; 610307, 
3445418; 608486, 3445689; 609111, 3442346; 610028, 3444758; 611184, 
3446370; 610272, 3445449; 608434, 3445711; 609162, 3442347; 610165, 
3445023; 611209, 3446400; 610237, 3445476; 608399, 3445728; 608365, 
3445755; 607200, 3445385; 605828, 3445088; 605381, 3446338; 605733, 
3447127; 608324, 3445791; 607175, 3445377; 605810, 3445098; 605351, 
3446369; 605738, 3447148; 608289, 3445822; 607157, 3445375; 605810, 
3445104; 605328, 3446404; 605738, 3447171; 608264, 3445861; 607145, 
3445367; 605782, 3445127; 605322, 3446437; 605734, 3447199; 608244, 
3445892; 607126, 3445355; 605767, 3445157; 605307, 3446461; 605733, 
3447221; 608233, 3445919; 607118, 3445338; 605771, 3445189; 605289, 
3446489; 605739, 3447247; 608217, 3445935; 607101, 3445330; 605779, 
3445226; 605279, 3446506; 605738, 3447260; 608194, 3445949; 607069, 
3445324; 605784, 3445267; 605268, 3446535; 605741, 3447270; 608164, 
3445949; 607044, 3445320; 605789, 3445288; 605258, 3446560; 605754, 
3447290; 608137, 3445929; 607017, 3445310; 605802, 3445309; 605254, 
3446583; 605769, 3447309; 608063, 3445876; 606983, 3445303; 605803, 
3445342; 605258, 3446604; 605779, 3447324; 607985, 3445824; 606950, 
3445295; 605800, 3445373; 605264, 3446626; 605784, 3447339; 607877, 
3445761; 606927, 3445289; 605794, 3445406; 605281, 3446641; 605795, 
3447355; 607860, 3445744; 606898, 3445275; 605789, 3445433; 605296, 
3446655; 605805, 3447372; 607838, 3445720; 606866, 3445265; 605787, 
3445475; 605309, 3446673; 605810, 3447382; 607817, 3445699; 606825, 
3445246; 605777, 3445512; 605322, 3446692; 605823, 3447398; 607793, 
3445689; 606796, 3445240; 605775, 3445551; 605353, 3446713; 605833, 
3447421; 607768, 3445685; 606757, 3445230; 605767, 3445584; 605378, 
3446736; 605835, 3447439; 607747, 3445693; 606732, 3445219; 605761, 
3445612; 605404, 3446742; 605823, 3447457; 607731, 3445707; 606691, 
3445199; 605749, 3445643; 605424, 3446756; 605826, 3447480; 607710, 
3445703; 606659, 3445189; 605738, 3445671; 605452, 3446759; 605841, 
3447508; 607684, 3445689; 606630, 3445187; 605741, 3445709; 605475, 
3446767; 605856, 3447533; 607637, 3445681; 606605, 3445189; 605761, 
3445732; 605499, 3446782; 605876, 3447549; 607618, 3445673; 606577, 
3445185; 605767, 3445770; 605529, 3446797; 605894, 3447571; 607592, 
3445658; 606548, 3445180; 605779, 3445796; 605534, 3446813; 605895, 
3447595; 607567, 3445632; 606507, 3445166; 605775, 3445827; 605550, 
3446821; 605882, 3447622; 607553, 3445613; 606458, 3445156; 605766, 
3445855; 605568, 3446835; 605876, 3447650; 607524, 3445601; 606417, 
3445141; 605759, 3445885; 605578, 3446846; 605869, 3447674; 607505, 
3445591; 606384, 3445129; 605754, 3445929; 605596, 3446862; 605879, 
3447709; 607464, 3445584; 606363, 3445125; 605756, 3445970; 605606, 
3446882; 605900, 3447725; 607444, 3445572; 606320, 3445117; 605751, 
3446006; 605609, 3446895; 605918, 3447724; 607419, 3445550; 606279, 
3445107; 605738, 3446024; 605613, 3446908; 605927, 3447714; 607411, 
3445527; 606248, 3445100; 605701, 3446049; 605628, 3446922; 605950, 
3447701; 607389, 3445521; 606220, 3445100; 605674, 3446070; 605636, 
3446931; 605966, 3447714; 607362, 3445515; 606195, 3445103; 605637, 
3446092; 605644, 3446948; 605978, 3447733; 607343, 3445515; 606169, 
3445094; 605598, 3446121; 605657, 3446969; 605979, 3447753; 607315, 
3445498; 606127, 3445094; 605570, 3446146; 605667, 3446977; 605978, 
3447770; 607292, 3445494; 606086, 3445086; 605544, 3446162; 605675, 
3447005; 605987, 3447789; 607276, 3445492; 606064, 3445082; 605511, 
3446177; 605685, 3447020; 605986, 3447814; 607251, 3445476; 606031, 
3445074; 605486, 3446190; 605695, 3447033; 605996, 3447821; 607239, 
3445463; 605998, 3445074; 605468, 3446217; 605701, 3447047; 606010, 
3447830; 607229, 3445435; 605959, 3445074; 605445, 3446251; 605710, 
3447058; 606025, 3447847; 607227, 3445412; 605922, 3445074; 605424, 
3446286; 605718, 3447083; 606037, 3447862; 607214, 3445404; 605863, 
3445080; 605407, 3446302; 605731, 3447112; 606048, 3447883; 606048, 
3447903; 606372, 3448573; 605898, 3449716; 604112, 3453023; 607252, 
3461523; 606048, 3447922; 606379, 3448593; 605845, 3449777; 604114, 
3453343; 607780, 3461019; 606056, 3447941; 606370, 3448609; 605792, 
3449843; 604112, 3453859; 608187, 3460561; 606071, 3447955; 606351, 
3448626; 605755, 3449904; 603180, 3453862; 608388, 3460205; 606088, 
3447962; 606339, 3448634; 605704, 3449943; 601371, 3453846; 608490, 
3460024; 606099, 3447990; 606314, 3448644; 605657, 3449993; 600479, 
3453854; 608742, 3459714; 606104, 3448005; 606295, 3448654; 605612, 
3450012; 600471, 3453415; 609049, 3459378; 606099, 3448026; 606282,

[[Page 10383]]

3448665; 605556, 3450044; 600056, 3453412; 609401, 3459156; 606089, 
3448037; 606268, 3448682; 605485, 3450105; 600058, 3454213; 609565, 
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[[Page 10384]]

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[[Page 10385]]

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[[Page 10386]]

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3537353; 655874, 3548701; 655605, 3547546; 655640, 3545600; 656048, 
3542221; 651856, 3536979; 655883, 3548688; 655594, 3547531; 655640, 
3545593; 656071, 3542172; 651945, 3536639; 655885, 3548669; 655578, 
3547510; 655575, 3545562; 656085, 3542141; 652009, 3536382; 655880, 
3548639; 655568, 3547494; 655566, 3545489; 656105, 3542092; 652050, 
3536220; 655871, 3548619; 655543, 3547460; 655548, 3545412; 656144, 
3541985; 651815, 3536198; 655868, 3548603; 655517, 3547427; 655537, 
3545283; 656181, 3541887; 651707, 3536194; 655872, 3548589; 655494, 
3547393; 655522, 3545197; 656216, 3541772; 651618, 3536213; 655877, 
3548564; 655455, 3547342; 655520, 3545178; 656251, 3541661; 651498, 
3536236; 655874, 3548545; 655432, 3547318; 655546, 3545083; 656251, 
3541661; 651348, 3536267; 655872, 3548530; 655423, 3547297; 655564, 
3545033; 656259, 3541637; 651247, 3536293; 655869, 3548514; 655411, 
3547282; 655593, 3544973; 656275, 3541576; 651171, 3536293; 655874, 
3548491; 655410, 3547267; 655612, 3544938; 656287, 3541523; 651098, 
3536271; 655876, 3548464; 655421, 3547258; 655632, 3544882; 655947, 
3541519; 651040, 3536213; 655874, 3548452; 655506, 3547168; 655708, 
3544740; 655947, 3541681; 650948, 3536115; 655840, 3548444; 655523, 
3547155; 655728, 3544687; 655948, 3541681; 650859, 3536004; 655808, 
3548437; 655577, 3547110; 655936, 3544696; 655936, 3542314; 650799, 
3535947; 655775, 3548442; 655725, 3546970; 655934, 3543323; 655562, 
3542314; 650771, 3535864; 655744, 3548455; 655754, 3546940; 655945, 
3543311; 655562, 3542314; 650732, 3535785; 655645, 3548516; 655850,

[[Page 10388]]

3546629; 655962, 3543295; 654352, 3542306; 650691, 3535677; 655609, 
3548550; 655846, 3546629; 655978, 3543276; 654352, 3542578; 650624, 
3535531; 655136, 3548812; 655852, 3546614; 655994, 3543259; 654085, 
3542408; 650574, 3535474; 655166, 3548212; 655864, 3546587; 656011, 
3543251; 653983, 3542314; 650497, 3535448; 655221, 3548218; 655868, 
3546565; 656025, 3543241; 653927, 3542202; 650444, 3535439; 655273, 
3548212; 655867, 3546546; 656049, 3543234; 653852, 3542071; 650405, 
3535410; 655329, 3548206; 655845, 3546543; 656062, 3543237; 653801, 
3542103; 650313, 3535324; 655359, 3548187; 655833, 3546549; 656076, 
3543246; 653580, 3541801; 650237, 3535232; 655390, 3548154; 655825, 
3546551; 656079, 3543257; 652968, 3540960; 650145, 3535159; 655409, 
3548121; 655811, 3546497; 656076, 3543270; 652793, 3540709; 650069, 
3535112; 655431, 3548083; 655798, 3546453; 656075, 3543283; 652676, 
3540557; 650031, 3535080; 655409, 3548055; 655785, 3546400; 656080, 
3543289; 652644, 3540509; 649986, 3535061; 655365, 3548013; 655765, 
3546343; 656083, 3543294; 652603, 3540420; 649948, 3535010; 655356, 
3547970; 655745, 3546296; 656092, 3543297; 652460, 3540062; 649878, 
3534889; 655358, 3547918; 655719, 3546248; 656111, 3543298; 652333, 
3539760; 649818, 3534804; 655363, 3547900; 655709, 3546221; 656130, 
3543296; 652202, 3539433; 649685, 3534661; 655384, 3547882; 655694, 
3546181; 656160, 3543281; 652009, 3538941; 649593, 3534543; 655398, 
3547866; 655692, 3546157; 656250, 3543223; 651917, 3538728; 649507, 
3534423; 655705, 3547677; 655690, 3546130; 656267, 3543213; 651879, 
3538617; 649453, 3534350; 655699, 3547668; 655673, 3546063; 656185, 
3543001; 651853, 3538509; 649402, 3534242; 655689, 3547651; 655649, 
3545991; 656185, 3543001; 651828, 3538366; 649326, 3534112; 655676, 
3547641; 655640, 3545940; 655980, 3542460; 651812, 3538198; 649259, 
3533953; 655664, 3547628; 655633, 3545910; 655979, 3542460; 651764, 
3538030; 649161, 3533731; 655654, 3547617; 655627, 3545871; 655952, 
3542389; 651758, 3537944; 649050, 3533448; 655644, 3547604; 655626, 
3545798; 655979, 3542346; 651752, 3537404; 649015, 3533369; 648580, 
3533362; 644760, 3531384; 647669, 3526453; 650551, 3521246; 644462, 
3520484; 647967, 3533353; 644636, 3531241; 647713, 3526460; 650421, 
3521094; 644500, 3520088; 647926, 3533353; 644582, 3531130; 647754, 
3526485; 650037, 3520688; 644481, 3520005; 647865, 3533340; 644564, 
3531117; 647821, 3526533; 649955, 3520599; 644459, 3519926; 647770, 
3533321; 644565, 3531110; 647891, 3526587; 649878, 3520440; 644405, 
3519856; 647643, 3533277; 644544,

3531067; 647942, 3526619; 649758, 3520148; 644316, 3519808; 647561, 
3533219; 644519, 3530997; 647996, 3526638; 649716, 3520024; 643966, 
3519599; 647465, 3533197; 644484, 3530879; 648015, 3526638; 649488, 
3520116; 643693, 3519440; 647399, 3533197; 644455, 3530711; 648040, 
3526615; 649154, 3520240; 643538, 3519338; 647335, 3533200; 644449, 
3530594; 648469, 3526219; 648897, 3520338; 643233, 3519167; 647275, 
3533184; 644452, 3530517; 648627, 3526082; 648853, 3520351; 643138, 
3519097; 647218, 3533153; 644395, 3530511; 648726, 3525961; 648789, 
3520354; 643058, 3519033; 647110, 3533115; 644354, 3530514; 648805, 
3525866; 648354, 3520354; 642982, 3518938; 646983, 3533070; 644370, 
3530397; 648891, 3525774; 647777, 3520351; 642874, 3518827; 646840, 
3533032; 644405, 3530273; 648973, 3525685; 647650, 3520351; 642757, 
3518722; 646741, 3533016; 644465, 3530102; 649040, 3525564; 647573, 
3520380; 642633, 3518675; 646678, 3533010; 644513, 3529962; 649113, 
3525444; 647519, 3520418; 642519, 3518649; 646583, 3533010; 644586, 
3529762; 649183, 3525326; 647443, 3520481; 642465, 3518611; 646497, 
3532997; 644659, 3529600; 649250, 3525212; 647354, 3520577; 642366, 
3518522; 646405, 3532975; 644754, 3529435; 649291, 3525107; 647278, 
3520637; 642188, 3518345; 646335, 3532959; 644808, 3529349; 649351, 
3524955; 647183, 3520681; 642036, 3518132; 646272, 3532902; 644840, 
3529254; 649402, 3524825; 647110, 3520691; 641969, 3518033; 646221, 
3532851; 644887, 3529063; 649453, 3524675; 647027, 3520688; 641852, 
3517808; 646126, 3532769; 644960, 3528768; 649485, 3524583; 646948, 
3520688; 641480, 3516887; 646078, 3532711; 645005, 3528603; 649501, 
3524498; 646808, 3520704; 641353, 3516614; 645992, 3532629; 645049, 
3528514; 649523, 3524412; 646691, 3520716; 641287, 3516541; 645941, 
3532613; 645138, 3528368; 649548, 3524355; 646529, 3520738; 641157, 
3516465; 645878, 3532613; 645243, 3528222; 649612, 3524282; 646367, 
3520754; 641026, 3516386; 645814, 3532626; 645405, 3528035; 649723, 
3524155; 646326, 3520755; 640925, 3516322; 645754, 3532638; 645468, 
3527968; 649764, 3524091; 646326, 3520761; 640763, 3516249; 645713, 
3532632; 645627, 3527816; 649777, 3524082; 646126, 3520792; 640601, 
3516179; 645662, 3532610; 645748, 3527701; 649777, 3524082; 645875, 
3520850; 640471, 3516112; 645608, 3532562; 645824, 3527650; 649897, 
3523850; 645710, 3520891; 640372, 3516065; 645557, 3532492; 645983, 
3527546; 649977, 3523701; 645513, 3520967; 640204, 3515966; 645443, 
3532318; 646056, 3527492; 650040, 3523656; 645341, 3521040; 640096, 
3515903; 645376, 3532238; 646465, 3527260; 650116, 3523612; 645183, 
3521104; 639934, 3515817; 645275, 3532118; 646538, 3527212; 650174, 
3523605; 645103, 3521167; 639845, 3515789; 645198, 3532010; 646649, 
3527136; 650139, 3523024; 645008, 3521243; 639750, 3515789; 645068, 
3531880; 646837, 3526977; 650123, 3522843; 644852, 3521370; 639655, 
3515785; 645040, 3531822; 647243, 3526663; 650136, 3522770; 644709, 
3521478; 639553, 3515776; 644973, 3531740; 647269, 3526628; 650113, 
3522691; 644643, 3521529; 639394, 3515754; 644925, 3531670; 647332, 
3526596; 650586, 3521472; 644621, 3521523; 639248, 3515738; 644881, 
3531575; 647586, 3526463; 650612, 3521393; 644567, 3521443; 639087, 
3515735; 644798, 3531476; 647627, 3526450; 650609, 3521326; 644557, 
3521358; 638909, 3515738; 638756, 3515741; 638289, 3510816; 634378, 
3509479; 624936, 3502867; 628776, 3496935; 638626, 3515741; 638217, 
3510734; 634394, 3508561; 624936, 3502632; 628782, 3496936; 638540, 
3515354; 638185, 3510701; 634396, 3507444; 624959, 3502521; 628781, 
3496912; 638515, 3515265; 638151, 3510681; 634195, 3507449; 624968, 
3502479; 628790, 3496912; 638493, 3515125; 637976, 3510569; 633235, 
3507431; 625093, 3502178; 628867, 3496911; 638467, 3514992; 637948, 
3510559; 632306, 3507412; 625213, 3501919; 628989, 3496912; 638486, 
3514954; 637936, 3510565; 632076, 3507413; 625370, 3501591; 629149, 
3496912; 638518, 3514833; 637918, 3510591; 632076, 3507412; 626064, 
3500139; 629164, 3496915; 638556, 3514760; 637896, 3510609; 631160, 
3507399; 626106, 3500014; 629325, 3496916; 638613, 3514677; 637886, 
3510608; 631139, 3509839; 626166, 3499843; 629427, 3496918; 638664, 
3514614; 637856, 3510602; 630998, 3509711; 626212, 3499691; 629439, 
3496920; 638709, 3514531; 637823, 3510625; 630868, 3509595; 626254, 
3499547; 629662, 3496922; 638744, 3514468; 637800, 3510640; 630374, 
3509161; 626295, 3499469; 629709,

[[Page 10389]]

3496922; 638759, 3514363; 637638, 3510553; 630244, 3509008; 626369, 
3499316; 629716, 3496925; 638750, 3514265; 637536, 3510469; 630138, 
3508865; 626415, 3499150; 629978, 3496929; 638747, 3514141; 637430, 
3510451; 629999, 3508666; 626457, 3498974; 629991, 3496932; 638748, 
3514107; 636824, 3510349; 629846, 3508393; 626489, 3498808; 630208, 
3496934; 638744, 3514079; 636704, 3510317; 629703, 3508231; 626499, 
3498701; 630247, 3496913; 638721, 3514013; 636662, 3510266; 629587, 
3508130; 626476, 3498558; 630277, 3496913; 638717, 3513979; 636611, 
3510233; 629412, 3508028; 626471, 3498401; 630282, 3496915; 638726, 
3513955; 636588, 3510247; 629236, 3507958; 626480, 3498276; 630384, 
3496918; 638807, 3513892; 636542, 3510257; 628866, 3507861; 626499, 
3498151; 630485, 3496918; 638813, 3513869; 636542, 3510312; 628607, 
3507792; 626526, 3497980; 630493, 3496921; 638786, 3513767; 636556, 
3510377; 628445, 3507764; 626531, 3497957; 630654, 3496924; 638775, 
3513703; 636621, 3510627; 628334, 3507760; 626536, 3497961; 630659, 
3496926; 638763, 3513590; 636630, 3510728; 628108, 3507760; 626660, 
3498008; 630817, 3496926; 638761, 3513540; 636579, 3510811; 627895, 
3507764; 626739, 3498031; 630894, 3496932; 638810, 3513392; 636177, 
3511163; 627770, 3507797; 626818, 3498031; 630982, 3496934; 638873, 
3513185; 635770, 3511514; 627632, 3507824; 626873, 3498035; 630998, 
3496936; 638898, 3512936; 635562, 3511690; 627534, 3507861; 626993, 
3498012; 631162, 3496939; 638919, 3512728; 635460, 3511769; 627488, 
3507880; 627090, 3497980; 631167, 3496941; 638938, 3512582; 635317, 
3511866; 627405, 3507884; 627206, 3497934; 631331, 3496943; 638933, 
3512481; 635261, 3511903; 627386, 3507880; 627373, 3497878; 631336, 
3496945; 638916, 3512347; 635183, 3511903; 627303, 3507843; 627479, 
3497841; 631417, 3496945; 638887, 3512231; 634410, 3511991; 627248, 
3507797; 627590, 3497818; 631826, 3496950; 638853, 3512074; 633721, 
3512097; 627035, 3507431; 628357, 3497679; 632090, 3496953; 638850, 
3512050; 633402, 3512166; 626984, 3507371; 628709, 3497610; 632086, 
3497757; 638858, 3511953; 633333, 3512176; 626933, 3507353; 628792, 
3497610; 632552, 3497752; 638855, 3511893; 632949, 3512176; 625763, 
3507348; 628755, 3497471; 632884, 3497751; 638835, 3511832; 632339, 
3511325; 625731, 3507251; 628752, 3497357; 632885, 3497681; 638749, 
3511612; 631826, 3510660; 625657, 3506863; 628752, 3497271; 632886, 
3497425; 638625, 3511211; 633003, 3510662; 625625, 3506636; 628770, 
3497154; 632889, 3497200; 638516, 3511085; 633876, 3510668; 625172, 
3504204; 628789, 3497074; 632891, 3496947; 638427, 3510976; 634350, 
3510676; 624977, 3503117; 628776, 3497006; 632893, 3496702; 632893, 
3496447; 632992, 3489361; 634467, 3485866; 633177, 3484760; 629839, 
3461806; 632895, 3496201; 632989, 3489062; 634450, 3485855; 633161, 
3484746; 629524, 3461660; 632899, 3495947; 632982, 3489066; 634431, 
3485838; 633144, 3484723; 629358, 3461581; 632898, 3495715; 632973, 
3489071; 634416, 3485821; 633125, 3484698; 629334, 3461559; 632899, 
3495588; 632961, 3489084; 634397, 3485796; 633112, 3484666; 629164, 
3461348; 632902, 3495459; 632943, 3489093; 634382, 3485778; 633109, 
3484643; 629088, 3461258; 632902, 3495340; 632928, 3489103; 634361, 
3485758; 633093, 3484627; 629067, 3461234; 632902, 3495275; 632895, 
3489116; 634345, 3485734; 633074, 3484610; 629035, 3461216; 632903, 
3495190; 632854, 3489143; 634328, 3485712; 633044, 3484578; 628987, 
3461205; 632903, 3495190; 632763, 3489202; 634292, 3485670; 633031, 
3484561; 628873, 3461163; 632912, 3494533; 632763, 3489203; 634236, 
3485612; 633024, 3484554; 628821, 3461147; 632801, 3494531; 632702, 
3489250; 634181, 3485557; 633042, 3481275; 628799, 3461141; 632784, 
3494569; 632670, 3489270; 634141, 3485523; 633106, 3478970; 628770, 
3461107; 632743, 3494628; 632614, 3489301; 634101, 3485499; 635695, 
3478295; 628318, 3460525; 632724, 3494664; 632570, 3489318; 634049, 
3485478; 635866, 3478295; 628309, 3460529; 632703, 3494699; 632577, 
3488940; 634012, 3485461; 635301, 3477352; 628184, 3460366; 632681, 
3494727; 632985, 3488945; 633991, 3485455; 635172, 3477172; 627754, 
3459840; 632637, 3494779; 632982, 3488876; 633963, 3485442; 634812, 
3476633; 627630, 3459658; 632604, 3494856; 632978, 3488668; 633926, 
3485419; 634589, 3476307; 627617, 3459613; 632518, 3495035; 632977, 
3488544; 633885, 3485389; 634358, 3475827; 627606, 3459570; 632500, 
3495061; 632973, 3488406; 633850, 3485365; 634204, 3475270; 627588, 
3459364; 632506, 3494899; 632970, 3488279; 633810, 3485367; 634118, 
3474696; 627466, 3457922; 632517, 3494241; 632969, 3488167; 633795, 
3485359; 634083, 3474532; 627447, 3457631; 632544, 3492923; 632970, 
3487996; 633760, 3485344; 634084, 3474407; 627447, 3457562; 632937, 
3492929; 633376, 3488006; 633730, 3485321; 633662, 3468424; 627461, 
3457496; 632940, 3492736; 633401, 3486379; 633705, 3485302; 633614, 
3468135; 627664, 3456813; 632945, 3492482; 633568, 3486380; 633656, 
3485269; 633397, 3467749; 627693, 3456742; 632950, 3492242; 633858, 
3486381; 633606, 3485227; 633336, 3467636; 627762, 3456641; 632952, 
3491990; 634145, 3486382; 633571, 3485186; 633244, 3467494; 627804, 
3456599; 632958, 3491739; 634412, 3486379; 633530, 3485141; 633225, 
3467462; 628048, 3456411; 632961, 3491502; 634608, 3486380; 633498, 
3485105; 633255, 3466022; 628630, 3455959; 632961, 3491292; 634605, 
3486357; 633472, 3485074; 633269, 3465351; 628723, 3455887; 633066, 
3491294; 634606, 3486336; 633455, 3485046; 633258, 3464185; 628746, 
3455869; 633199, 3491293; 634608, 3486313; 633436, 3485014; 633261, 
3464067; 628770, 3455832; 633334, 3491296; 634603, 3486274; 633413, 
3484993; 632852, 3463963; 628834, 3455758; 633466, 3491296; 634594, 
3486212; 633395, 3484991; 632527, 3463897; 628979, 3455572; 633596, 
3491297; 634583, 3486164; 633376, 3484977; 632098, 3463776; 629252, 
3455218; 633832, 3491300; 634561, 3486105; 633352, 3484949; 631666, 
3463600; 629889, 3454392; 633831, 3490506; 634524, 3486014; 633321, 
3484915; 631263, 3463378; 630059, 3454159; 632989, 3490495; 634512, 
3485988; 633297, 3484881; 630865, 3463131; 630188, 3453990; 632171, 
3490491; 634507, 3485963; 633271, 3484849; 630540, 3462834; 630230, 
3453934; 632184, 3489673; 634495, 3485935; 633246, 3484820; 630265, 
3462475; 631288, 3453835; 632996, 3489690; 634480, 3485914; 633219, 
3484793; 630014, 3462099; 631720, 3454819; 632995, 3489610; 634475, 
3485878; 633198, 3484776; 629971, 3462038; 632153, 3454465; 632650, 
3454111; 633274, 3453516; 633566, 3453131; 633635, 3453079; 633868, 
3452726; 634063, 3452327; 634223, 3451958; 634338, 3451217; 634382, 
3450854; 634356, 3450389; 634275, 3450112; 634241, 3449864; 633676, 
3449861; 633723, 3449540; 633583, 3448502; 633171, 3447753; 632488, 
3447108; 631964, 3446518; 631534, 3445999; 631072, 3445114; 630997, 
3443829; 631384, 3442719; 632210, 3441980; 633594, 3440733; 634405, 
3439685; 635378, 3438749; 636938, 3437365; 637247, 3436192; 637072, 
3435194; 636773, 3434209; 635837, 3433273; 635288, 3432804; 634103,

[[Page 10390]]

3432193; 632669, 3431519; 631309, 3431132; 630236, 3430683; 629550, 
3430259; 628989, 3429735; 628278, 3429149; 627903, 3428941; 627696, 
3428995; 627611, 3429276; 627488, 3429768; 627488, 3430042; 627684, 
3430417; 627584, 3430657; 627261, 3431025; 627070, 3431218.
    (ii) Note: Map of Unit 1, Tensas River Basin (Map 2), follows:
BILLING CODE 4310-55-P

[[Page 10391]]

[GRAPHIC] [TIFF OMITTED] TR10MR09.001

BILLING CODE 4310-55-C

[[Page 10392]]

    (7) Unit 2: Upper Atchafalaya River Basin. Iberia, Iberville, 
Pointe Coupee, St. Martin, and St. Mary Parishes, Louisiana.
    (i) From USGS 1:24,000 scale digital ortho-photo quarter-
quadrangles: Batchelor NE; Batchelor NW; Batchelor SE; Batchelor SW; 
Bayou Current NE; Bayou Current NW; Bayou Current SE; Big Bend SE; 
Butte La Rose NE; Butte La Rose NW; Butte La Rose SE; Butte La Rose SW; 
Catahoula NE; Catahoula NW; Catahoula SE; Catahoula SW; Centerville NE; 
Centerville NE SW; Centerville NW; Centerville NW NE; Centerville NW 
NW; Centerville NW SE; Centerville NW SW; Centerville SE; Charenton NE; 
Charenton SE; Cow Bayou NW; Cow Bayou SW; Erwinville NW; Fordoche NE; 
Fordoche NW; Fordoche SW; Grand River SW; Innis NE; Innis NW; Innis SE; 
Innis Jackass Bay NE; Jackass Bay NW; Jackass Bay SE; Jackass Bay SW; 
Krotz Springs NE; Krotz Springs SE; Lacour SW; Lake Chicot NW; Lake 
Chicot SW; Lake Mongoulois NE; Lake Mongoulois NW; Lake Mongoulois SE; 
Lake Mongoulois SW; Loreauville NE; Lottie NE; Lottie NW; Lottie SE; 
Lottie SW; Maringouin NE; Maringouin NW; Maringouin NW NE; Maringouin 
NW NW; Maringouin NW SE; Maringouin NW SW; Maringouin SE; Maringouin 
SW; Melville NE; Melville NW; Melville SE; Melville SW; Morganza NE; 
Morganza NW; Morganza SE; Morganza SW; New Roads NW; New Roads SW; 
North Bend NE; Patterson NE; Patterson NW; Portage NE; Simmesport NE; 
Simmesport SE; Swayze Lake NE; Tiger Island NW; Tiger Island SE; Tiger 
Island SW; Turnbull Island SE; Turnbull Island SW; Louisiana. Land 
bounded by the following UTM Zone 15N, North American Datum of 1983 
(NAD83) coordinates (E, N): 627070, 3431218; 622846, 3423182; 633656, 
3402371; 632966, 3398656; 646698, 3394803; 624888, 3428860; 622925, 
3423142; 633606, 3402336; 634014, 3398693; 646362, 3394427; 624679, 
3428635; 623229, 3423055; 633535, 3402289; 635504, 3398712; 646209, 
3394250; 624539, 3428524; 623782, 3422928; 633479, 3402262; 635494, 
3399338; 646050, 3394104; 624367, 3428418; 623915, 3422888; 633437, 
3402238; 635494, 3399372; 645933, 3393974; 624042, 3428281; 623970, 
3422841; 633381, 3402196; 635496, 3399396; 645881, 3393906; 623468, 
3428034; 624010, 3422775; 633347, 3402167; 635544, 3399422; 645661, 
3393580; 622430, 3427587; 624036, 3422708; 633323, 3402151; 635846, 
3399597; 645589, 3393480; 622200, 3427492; 624039, 3422621; 633302, 
3402130; 635918, 3399551; 645468, 3393332; 622060, 3427426; 624042, 
3422497; 632779, 3401762; 635951, 3399527; 645404, 3393228; 621981, 
3427370; 624039, 3422327; 632003, 3401548; 636040, 3399480; 645322, 
3393064; 621946, 3427328; 624050, 3422216; 631942, 3401534; 636154, 
3399421; 645108, 3392480; 621888, 3427251; 624055, 3422145; 631868, 
3401529; 636341, 3399358; 645050, 3392257; 621854, 3427180; 624132, 
3421909; 631820, 3401532; 636450, 3399338; 645002, 3392091; 621814, 
3427087; 624288, 3421478; 631688, 3401561; 636619, 3399306; 644968, 
3392022; 621782, 3426973; 624843, 3419975; 631595, 3401595; 636803, 
3399280; 644920, 3391961; 621774, 3426865; 625373, 3418525; 631444, 
3401622; 638372, 3399028; 644865, 3391903; 621777, 3426770; 625833, 
3417279; 631354, 3401654; 639888, 3398792; 644838, 3391853; 621795, 
3426685; 625936, 3417054; 631026, 3401733; 639989, 3398792; 644806, 
3391781; 621832, 3426561; 625962, 3417024; 630897, 3401765; 640124, 
3398777; 644788, 3391681; 621891, 3426354; 626014, 3416951; 630831, 
3401783; 640202, 3398766; 644767, 3391588; 622102, 3425785; 626081, 
3416850; 630783, 3401796; 640415, 3398730; 644756, 3391522; 622166, 
3425584; 626130, 3416712; 630741, 3401799; 640875, 3398660; 644751, 
3391503; 622190, 3425518; 626156, 3416598; 630669, 3401788; 641602, 
3398540; 644752, 3391502; 622206, 3425449; 626172, 3416494; 630555, 
3401767; 641752, 3398520; 644732, 3391408; 622208, 3425338; 626208, 
3416310; 630630, 3401728; 643510, 3398236; 644730, 3391367; 622198, 
3425217; 626245, 3416157; 630641, 3401712; 644243, 3398125; 644774, 
3391009; 622198, 3425132; 626297, 3415988; 630659, 3401601; 644367, 
3398096; 644825, 3390779; 622161, 3425042; 626478, 3415492; 630624, 
3401603; 644461, 3398075; 644857, 3390588; 622116, 3424955; 626629, 
3415167; 630608, 3401598; 644591, 3398044; 644873, 3390432; 622081, 
3424870; 626704, 3415027; 630606, 3401582; 644848, 3398005; 644888, 
3390340; 622055, 3424793; 627548, 3413586; 630860, 3401180; 645996, 
3397829; 644894, 3390274; 622020, 3424693; 628405, 3412111; 630862, 
3401135; 645967, 3397408; 644915, 3390194; 622007, 3424621; 629298, 
3410581; 630897, 3401138; 645967, 3397317; 644949, 3390054; 621997, 
3424529; 630119, 3409164; 630966, 3401124; 645985, 3397247; 644973, 
3389977; 621994, 3424465; 630257, 3408873; 631164, 3401079; 645998, 
3397198; 645031, 3389853; 622002, 3424373; 630475, 3408413; 631249, 
3401058; 646032, 3397133; 645121, 3389633; 622084, 3423880; 630838, 
3407782; 631347, 3401042; 646097, 3397045; 645187, 3389509; 622094, 
3423830; 631690, 3406320; 631394, 3401042; 646164, 3396946; 644957, 
3389403; 622079, 3423785; 632560, 3404835; 631455, 3401053; 646325, 
3396736; 643801, 3388837; 622065, 3423764; 633471, 3403277; 631677, 
3401124; 646316, 3396727; 642843, 3388374; 622192, 3423642; 633907, 
3402558; 631677, 3401008; 646441, 3396572; 642679, 3388300; 622258, 
3423576; 633820, 3402511; 631682, 3400747; 647313, 3395378; 642642, 
3388271; 622330, 3423510; 633786, 3402484; 631738, 3399415; 647174, 
3395300; 642597, 3388226; 622391, 3423468; 633762, 3402445; 631738, 
3398944; 647021, 3395173; 642296, 3387903; 622568, 3423362; 633744, 
3402431; 632249, 3398648; 646849, 3394988; 642256, 3387853; 642221, 
3387829; 640139, 3384635; 639353, 3383407; 636625, 3383452; 628698, 
3381254; 642147, 3387808; 640081, 3384608; 639345, 3383362; 636578, 
3383487; 628694, 3381254; 642028, 3387773; 640005, 3384583; 639335, 
3383328; 636519, 3383516; 628702, 3381206; 641962, 3387752; 639963, 
3384576; 639319, 3383296; 636403, 3383553; 628720, 3380959; 641883, 
3387728; 639922, 3384556; 639292, 3383273; 636191, 3383616; 628744, 
3380645; 641825, 3387689; 639867, 3384566; 639239, 3383273; 636136, 
3383627; 628760, 3380534; 641750, 3387622; 639842, 3384593; 639186, 
3383280; 636075, 3383632; 628792, 3380425; 641713, 3387580; 639814, 
3384614; 639120, 3383280; 635734, 3383587; 628847, 3380309; 641563, 
3387395; 639770, 3384621; 639073, 3383262; 635535, 3383556; 628908, 
3380208; 641489, 3387313; 639736, 3384646; 639020, 3383230; 635514, 
3383550; 628958, 3380142; 641438, 3387220; 639707, 3384672; 638991, 
3383185; 635490, 3383537; 629120, 3379981; 641428, 3387186; 639676, 
3384671; 638964, 3383143; 635453, 3383508; 630059, 3379015; 641404, 
3387117; 639652, 3384664; 638927, 3383087; 635419, 3383500; 630194, 
3378880; 641375, 3386998; 639610, 3384678; 638872, 3383050; 635384, 
3383471; 630294, 3378785; 641330, 3386839; 639564, 3384651; 638832, 
3383008; 635368, 3383445; 630390, 3378718; 641293, 3386699; 639552, 
3384614; 638784, 3382968; 635339, 3383407; 630456, 3378679; 641242, 
3386535; 639535, 3384579; 638750, 3382934; 635316, 3383384; 630519, 
3378647;

[[Page 10393]]

641213, 3386424; 639522, 3384547; 638721, 3382913; 634905, 3383079; 
630591, 3378610; 641105, 3386067; 639527, 3384511; 638697, 3382870; 
634884, 3383053; 630765, 3378546; 641076, 3385940; 639549, 3384484; 
638673, 3382831; 634871, 3383021; 631271, 3378343; 641057, 3385831; 
639620, 3384461; 638636, 3382799; 634871, 3383000; 631866, 3378107; 
641049, 3385702; 639655, 3384413; 638602, 3382767; 634882, 3382971; 
632065, 3378025; 641049, 3385508; 639655, 3384365; 638554, 3382727; 
634929, 3382910; 632239, 3377975; 641052, 3385463; 639623, 3384320; 
638512, 3382688; 634939, 3382880; 632586, 3377877; 641110, 3385270; 
639586, 3384294; 638477, 3382640; 634934, 3382855; 633006, 3377763; 
641115, 3385244; 639525, 3384267; 638464, 3382614; 635368, 3382326; 
633126, 3377734; 641123, 3385019; 639483, 3384230; 638438, 3382624; 
636285, 3381183; 633274, 3377684; 641123, 3384889; 639472, 3384193; 
638385, 3382529; 635295, 3381186; 633790, 3377491; 641134, 3384828; 
639462, 3384138; 638361, 3382545; 634420, 3381205; 634104, 3377374; 
641160, 3384773; 639454, 3384080; 638321, 3382561; 634179, 3381200; 
634226, 3377329; 641216, 3384731; 639443, 3384000; 638276, 3382590; 
633198, 3381222; 634263, 3377308; 641280, 3384699; 639443, 3383942; 
638239, 3382603; 631550, 3381246; 634874, 3376964; 641356, 3384656; 
639472, 3383915; 638125, 3382656; 631333, 3381259; 635208, 3376782; 
641396, 3384643; 639493, 3383865; 638067, 3382690; 631196, 3381275; 
635269, 3376745; 641391, 3384585; 639536, 3383799; 638020, 3382709; 
630857, 3381307; 635330, 3376700; 641269, 3384582; 639565, 3383717; 
637983, 3382730; 630783, 3381315; 635385, 3376647; 641139, 3384588; 
639589, 3383667; 637935, 3382735; 630693, 3381323; 636623, 3375541; 
641033, 3384574; 639604, 3383603; 637903, 3382749; 630613, 3381323; 
637846, 3374453; 640946, 3384559; 639607, 3383558; 637800, 3382762; 
630494, 3381320; 637917, 3374387; 640883, 3384572; 639581, 3383527; 
637445, 3382778; 630336, 3381312; 637989, 3374303; 640798, 3384601; 
639544, 3383505; 637387, 3382783; 630047, 3381302; 638182, 3374072; 
640711, 3384633; 639499, 3383511; 637340, 3382804; 629902, 3381288; 
639110, 3372980; 640634, 3384646; 639456, 3383511; 637022, 3383021; 
629717, 3381283; 639198, 3372876; 640520, 3384662; 639422, 3383503; 
636848, 3383228; 629238, 3381288; 639251, 3372781; 640377, 3384662; 
639393, 3383474; 636755, 3383333; 629150, 3381286; 639285, 3372673; 
640226, 3384656; 639364, 3383447; 636728, 3383370; 629005, 3381283; 
639618, 3371511; 639925, 3370442; 642964, 3364183; 635436, 3350403; 
641982, 3339188; 647361, 3327687; 639941, 3370395; 643004, 3364124; 
635624, 3350218; 642000, 3338867; 647294, 3327386; 639949, 3370355; 
643022, 3364061; 635820, 3349983; 641942, 3338513; 647194, 3327126; 
639947, 3370329; 643035, 3363990; 635941, 3349715; 641894, 3338211; 
647040, 3326901; 639928, 3370284; 641263, 3363413; 635976, 3349485; 
641860, 3337997; 646921, 3326743; 639899, 3370220; 639760, 3362926; 
635947, 3349387; 641847, 3337687; 646683, 3326571; 639891, 3370191; 
638043, 3362365; 635923, 3349186; 641905, 3337394; 646345, 3326372; 
639944, 3370006; 636556, 3361878; 635835, 3349009; 642117, 3337087; 
646125, 3326219; 640222, 3369069; 635191, 3361434; 635745, 3348821; 
642267, 3336931; 646003, 3326068; 640243, 3368992; 633944, 3361029; 
635655, 3348636; 642429, 3336685; 645850, 3325809; 640251, 3368958; 
632338, 3360502; 635616, 3348477; 642741, 3336330; 645747, 3325478; 
640248, 3368916; 631046, 3360107; 635613, 3348300; 643011, 3335989; 
645651, 3325034; 640240, 3368873; 630832, 3360037; 635658, 3348088; 
643373, 3335549; 645588, 3324285; 640253, 3368831; 630888, 3359920; 
635756, 3347982; 643569, 3335370; 645577, 3324055; 640343, 3368524; 
630967, 3359714; 635973, 3347776; 643799, 3335161; 645516, 3323597; 
640388, 3368386; 631049, 3359436; 636293, 3347564; 644059, 3334938; 
645490, 3322930; 641179, 3367027; 631107, 3359142; 636582, 3347355; 
644233, 3334766; 645495, 3322533; 641176, 3367026; 631181, 3358809; 
636952, 3347114; 644419, 3334563; 645556, 3322179; 641199, 3366993; 
631269, 3358333; 637235, 3346937; 644546, 3334332; 645638, 3321882; 
641337, 3366752; 631351, 3357949; 637571, 3346768; 644643, 3334147; 
645813, 3321520; 641437, 3366580; 631472, 3357661; 637894, 3346561; 
644733, 3333922; 646027, 3321144; 641477, 3366511; 631636, 3357169; 
638116, 3346368; 644844, 3333684; 646427, 3320522; 641829, 3365701; 
631771, 3356809; 638251, 3346228; 644987, 3333488; 646654, 3320120; 
641871, 3365603; 631877, 3356486; 638444, 3345964; 645117, 3333385; 
646884, 3319755; 641903, 3365559; 631965, 3356203; 638555, 3345649; 
645268, 3333285; 647324, 3319131; 641982, 3365503; 632052, 3355827; 
638669, 3345191; 645517, 3333155; 647649, 3318789; 642027, 3365455; 
632163, 3355444; 638722, 3344950; 645786, 3333025; 647882, 3318456; 
642049, 3365434; 632314, 3354957; 638748, 3344850; 646011, 3332885; 
647924, 3318380; 642062, 3365408; 632388, 3354689; 638865, 3344635; 
646212, 3332713; 648218, 3318515; 642131, 3365080; 632446, 3354470; 
639161, 3344281; 646400, 3332541; 649246, 3318965; 642149, 3365021; 
632541, 3354137; 639431, 3343976; 646519, 3332369; 649984, 3319318; 
642160, 3365000; 632597, 3353951; 639648, 3343728; 646583, 3332187; 
650094, 3318803; 642194, 3364963; 632658, 3353761; 640045, 3343191; 
646654, 3331962; 650269, 3318425; 642218, 3364942; 632721, 3353562; 
640778, 3342378; 646699, 3331716; 650349, 3317885; 642231, 3364918; 
632846, 3353396; 640979, 3342193; 646794, 3331396; 650458, 3317341; 
642279, 3364770; 632949, 3353218; 641072, 3342013; 646829, 3331054; 
650641, 3316710; 642340, 3364561; 633213, 3352914; 641209, 3341802; 
646845, 3330649; 650971, 3316118; 642358, 3364503; 633420, 3352710; 
641410, 3341574; 646863, 3330537; 651409, 3315613; 642382, 3364479; 
633623, 3352488; 641548, 3341389; 646853, 3330143; 651870, 3315103; 
642408, 3364479; 633851, 3352216; 641669, 3341204; 646847, 3329817; 
652218, 3314835; 642451, 3364484; 633981, 3351985; 641767, 3340947; 
646903, 3329497; 652496, 3314789; 642493, 3364490; 634174, 3351718; 
641834, 3340661; 646982, 3329172; 653092, 3314154; 642514, 3364492; 
634404, 3351409; 641860, 3340304; 647159, 3328727; 653501, 3313549; 
642541, 3364490; 634613, 3351173; 641884, 3339944; 647292, 3328415; 
653656, 3313255; 642623, 3364434; 634923, 3350856; 641902, 3339558; 
647337, 3328174; 653863, 3312929; 642932, 3364233; 635087, 3350686; 
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657231, 3304726; 658375, 3296693; 664568, 3290025; 660530, 3290620; 
654779, 3312040; 657268, 3304633; 658774, 3295820; 664569, 3290010; 
660491, 3290514; 655085, 3311727; 657295, 3304525; 659272, 3295259; 
664568, 3289995; 660483, 3290487; 655520, 3311187; 657329, 3304403; 
660366, 3294671; 664561, 3289975; 660459, 3290471; 655821, 3310703; 
657353, 3304303; 661615, 3293839; 664562, 3289939; 660430, 3290453; 
656152, 3310123; 657379, 3304192; 662046, 3293586; 664536, 3289918; 
659475, 3289874; 656420, 3309433; 657400, 3304139; 662613, 3293297;

[[Page 10394]]

664409, 3290106; 658988, 3289580; 656706, 3308621; 657427, 3304096; 
663166, 3293083; 664330, 3290210; 658943, 3289548; 656727, 3308069; 
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658572, 3289125; 656524, 3307243; 657609, 3303993; 663854, 3292615; 
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657397, 3287600; 656652, 3306599; 657238, 3302556; 664483, 3291728; 
662700, 3290667; 657590, 3288219; 656617, 3306560; 657208, 3302426; 
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657171, 3302243; 664438, 3291588; 662409, 3290810; 657429, 3289865; 
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657393, 3290148; 656593, 3306398; 657116, 3301931; 664459, 3291440; 
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664483, 3291374; 662205, 3290895; 657270, 3290702; 656625, 3306263; 
657105, 3301338; 664515, 3291281; 662150, 3290905; 657025, 3291234; 
656649, 3306171; 657103, 3301182; 664541, 3291181; 662102, 3290911; 
656916, 3291377; 656662, 3306091; 657100, 3301066; 664581, 3291067; 
661890, 3290934; 656807, 3291530; 656697, 3306004; 657095, 3300931; 
664600, 3290982; 661779, 3290945; 656704, 3291668; 656720, 3305906; 
657103, 3300759; 664616, 3290921; 661739, 3290948; 655916, 3292737; 
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655754, 3292959; 656752, 3305755; 657116, 3300516; 664653, 3290733; 
661605, 3290990; 655522, 3293271; 656771, 3305676; 657066, 3300460; 
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656986, 3300394; 664668, 3290506; 661406, 3291064; 655231, 3293676; 
656829, 3305477; 656883, 3300367; 664676, 3290384; 661332, 3291085; 
655180, 3293747; 656863, 3305393; 656819, 3300254; 664682, 3290262; 
661287, 3291091; 655133, 3293800; 656908, 3305290; 656748, 3300079; 
664687, 3290220; 661258, 3291093; 655059, 3293869; 656956, 3305210; 
656740, 3299862; 664682, 3290196; 661200, 3291083; 654717, 3294181; 
656982, 3305144; 656756, 3299621; 664679, 3290172; 661004, 3290972; 
654170, 3294700; 657043, 3305067; 656819, 3299455; 664663, 3290120; 
660821, 3290866; 654143, 3294745; 657107, 3304996; 656952, 3299002; 
664639, 3290075; 660594, 3290741; 654125, 3294800; 657141, 3304924; 
657199, 3298261; 664608, 3290061; 660575, 3290718; 654013, 3295343; 
657189, 3304840; 657591, 3297607; 664580, 3290045; 660554, 3290688; 
653765, 3296608; 653640, 3297245; 649928, 3304863; 644569, 3311553; 
646125, 3314913; 643196, 3316922; 653630, 3297311; 649915, 3304902; 
644388, 3311790; 646165, 3314937; 643071, 3316996; 653619, 3297396; 
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653606, 3297449; 650058, 3305458; 644139, 3312525; 646079, 3314936; 
642955, 3317044; 653505, 3297957; 650233, 3306130; 644167, 3312802; 
646041, 3314916; 642894, 3317039; 653466, 3298110; 650267, 3306241; 
644151, 3313172; 646014, 3314943; 642796, 3317036; 653405, 3298412; 
650280, 3306328; 644168, 3313523; 645921, 3314967; 642717, 3317028; 
653400, 3298481; 650283, 3306394; 644331, 3313868; 645899, 3315009; 
642632, 3317039; 653341, 3299402; 650256, 3306439; 644721, 3314357; 
645939, 3315005; 642566, 3317047; 653307, 3299910; 650217, 3306474; 
644992, 3314536; 645973, 3314996; 642452, 3317089; 653254, 3300674; 
650166, 3306492; 645212, 3314638; 645995, 3315009; 642315, 3317200; 
653222, 3301071; 650135, 3306492; 645379, 3314723; 645984, 3315026; 
642127, 3317367; 653214, 3301113; 650069, 3306490; 645525, 3314789; 
645974, 3315043; 642005, 3317565; 653185, 3301166; 649894, 3306466; 
645645, 3314899; 646002, 3315045; 641695, 3317959; 653146, 3301209; 
649145, 3306365; 645727, 3314932; 646040, 3315017; 641465, 3318319; 
653077, 3301246; 649142, 3306397; 645754, 3314852; 646071, 3315037; 
641349, 3318489; 653021, 3301248; 649146, 3306556; 645678, 3314735; 
646061, 3315076; 641227, 3318671; 652929, 3301248; 649211, 3306658; 
645706, 3314626; 646017, 3315121; 641042, 3318928; 652860, 3301238; 
648998, 3306713; 645834, 3314579; 645959, 3315169; 640915, 3319131; 
652825, 3301230; 648645, 3306761; 645878, 3314558; 645904, 3315178; 
640809, 3319258; 652736, 3301198; 648493, 3306776; 645937, 3314498; 
645925, 3315294; 640701, 3319420; 652691, 3301193; 648381, 3306807; 
645976, 3314500; 645908, 3315438; 640603, 3319560; 652627, 3301211; 
648218, 3306841; 645919, 3314561; 645908, 3315507; 640560, 3319624; 
651997, 3301394; 647956, 3306950; 645800, 3314614; 645938, 3315688; 
640513, 3319729; 651921, 3301420; 647750, 3307123; 645712, 3314658; 
645927, 3315807; 640431, 3319893; 651878, 3301452; 647478, 3307375; 
645703, 3314734; 645894, 3315930; 640211, 3320264; 651833, 3301500; 
647206, 3307634; 645753, 3314782; 645885, 3316087; 640129, 3320386; 
651799, 3301571; 647072, 3307769; 645767, 3314745; 645796, 3316261; 
640050, 3320531; 651772, 3301661; 646989, 3307949; 645815, 3314767; 
645680, 3316369; 639907, 3320700; 651751, 3301748; 646857, 3308067; 
645868, 3314770; 645545, 3316457; 639748, 3320965; 651690, 3301992; 
646738, 3308247; 645926, 3314792; 645397, 3316515; 639645, 3321063; 
651680, 3302013; 646592, 3308551; 645911, 3314840; 645262, 3316544; 
639513, 3321214; 651637, 3302058; 646455, 3308737; 645932, 3314850; 
645148, 3316547; 639364, 3321373; 651619, 3302082; 646222, 3308979; 
645998, 3314762; 645003, 3316552; 638968, 3321830; 651587, 3302206; 
646474, 3309445; 646036, 3314727; 644907, 3316549; 638560, 3322338; 
651450, 3302743; 646273, 3309542; 646079, 3314702; 644820, 3316554; 
638354, 3322627; 651415, 3302873; 646046, 3309684; 646074, 3314649; 
644683, 3316602; 638258, 3322746; 651399, 3302910; 645913, 3309844; 
646087, 3314652; 644548, 3316639; 638118, 3322971; 651365, 3302971; 
645780, 3310026; 646095, 3314703; 644357, 3316689; 637925, 3323243; 
651227, 3303209; 645583, 3310262; 646133, 3314660; 644201, 3316734; 
637798, 3323420; 651190, 3303267; 645404, 3310470; 646173, 3314693; 
644026, 3316771; 637168, 3324370; 651061, 3303418; 645302, 3310602; 
646160, 3314761; 643831, 3316811; 636697, 3325071; 650799, 3303735;

[[Page 10395]]

645173, 3310819; 646137, 3314812; 643637, 3316848; 636478, 3325413; 
650701, 3303847; 645066, 3310995; 646095, 3314817; 643473, 3316859; 
636269, 3325775; 650410, 3304235; 644909, 3311180; 646089, 3314862; 
643362, 3316875; 636131, 3326077; 650240, 3304455; 644760, 3311373; 
646086, 3314893; 643251, 3316898; 636028, 3326291; 635986, 3326336; 
631191, 3332448; 626185, 3340774; 625604, 3345476; 627376, 3348394; 
635963, 3326376; 631019, 3332601; 626172, 3340854; 625620, 3345540; 
627347, 3348463; 635829, 3326550; 630831, 3332734; 626153, 3340907; 
625646, 3345571; 627321, 3348548; 635699, 3326630; 630516, 3332908; 
626150, 3340941; 625694, 3345585; 627279, 3348723; 635432, 3326712; 
630304, 3333011; 626172, 3340962; 625744, 3345585; 627236, 3348868; 
635173, 3326762; 630164, 3333056; 626177, 3340997; 625792, 3345598; 
627175, 3349064; 634956, 3326825; 629989, 3333133; 626174, 3341047; 
625855, 3345619; 627128, 3349223; 634699, 3326915; 629204, 3333588; 
626148, 3341094; 626072, 3345722; 627075, 3349355; 634437, 3327005; 
629093, 3333572; 626140, 3341153; 626130, 3345743; 627011, 3349511; 
634292, 3327095; 628370, 3333975; 626137, 3341206; 626188, 3345770; 
626948, 3349646; 634196, 3327185; 628227, 3334070; 626137, 3341256; 
626241, 3345775; 626898, 3349754; 633987, 3327307; 628079, 3334186; 
626137, 3341322; 626321, 3345791; 626855, 3349828; 633762, 3327384; 
627920, 3334319; 626142, 3341364; 626382, 3345812; 626810, 3349921; 
633569, 3327421; 627796, 3334488; 626137, 3341452; 626487, 3345844; 
626734, 3350082; 633387, 3327453; 627569, 3334834; 626137, 3341534; 
626575, 3345870; 626673, 3350167; 633276, 3327495; 627354, 3335197; 
626132, 3341621; 626715, 3345926; 626607, 3350265; 633167, 3327580; 
627309, 3335290; 626129, 3341698; 626789, 3345974; 626564, 3350344; 
633085, 3327714; 627203, 3335541; 626116, 3341801; 626982, 3346082; 
626554, 3350416; 633024, 3327847; 627293, 3335660; 626097, 3341901; 
627112, 3346156; 626535, 3350511; 632985, 3327979; 627383, 3335845; 
626087, 3341968; 627242, 3346228; 626519, 3350604; 632971, 3328127; 
627611, 3336271; 626071, 3342103; 627337, 3346286; 626482, 3350646; 
632993, 3328228; 627640, 3336390; 626071, 3342187; 627406, 3346310; 
626376, 3350699; 633037, 3328339; 627658, 3336515; 626055, 3342243; 
627517, 3346344; 626326, 3350757; 633096, 3328458; 627664, 3336673; 
626037, 3342293; 627702, 3346405; 626284, 3350823; 633120, 3328529; 
627658, 3336864; 626010, 3342343; 627935, 3346479; 626255, 3350934; 
633109, 3328601; 627658, 3336991; 625992, 3342391; 628146, 3346553; 
626231, 3351059; 633085, 3328736; 627624, 3337110; 625981, 3342465; 
628244, 3346582; 626247, 3351231; 633053, 3328802; 627545, 3337271; 
625973, 3342539; 628342, 3346603; 626284, 3351538; 633043, 3328895; 
627256, 3337557; 625952, 3342648; 628345, 3346653; 626323, 3351744; 
633022, 3328987; 627092, 3337753; 625941, 3342796; 628308, 3346704; 
626339, 3351956; 633011, 3329096; 626994, 3337835; 625933, 3342941; 
628226, 3346783; 626350, 3352194; 633000, 3329180; 626857, 3338012; 
625925, 3343055; 628154, 3346886; 626339, 3352324; 632961, 3329299; 
626769, 3338123; 625902, 3343211; 628014, 3347079; 626297, 3352482; 
632926, 3329408; 626595, 3338303; 625883, 3343425; 627802, 3347413; 
626220, 3352765; 632836, 3329768; 626513, 3338430; 625873, 3343529; 
627742, 3347479; 626186, 3352911; 632760, 3330122; 626383, 3338692; 
625813, 3344140; 627689, 3347564; 626091, 3353226; 632746, 3330228; 
626293, 3338954; 625789, 3344410; 627641, 3347669; 625863, 3353744; 
632728, 3330313; 626314, 3339594; 625770, 3344661; 627609, 3347725; 
625686, 3354221; 632678, 3330374; 626328, 3339819; 625768, 3344801; 
627540, 3347863; 625670, 3354430; 632609, 3330416; 626359, 3340063; 
625760, 3344920; 627519, 3347908; 625733, 3354633; 632241, 3331149; 
626357, 3340137; 625744, 3345016; 627493, 3347974; 625874, 3354861; 
632006, 3331559; 626341, 3340216; 625670, 3345204; 627458, 3348098; 
626016, 3355107; 631897, 3331749; 626314, 3340340; 625665, 3345251; 
627443, 3348183; 626112, 3355313; 631844, 3331818; 626291, 3340425; 
625662, 3345288; 627424, 3348252; 626157, 3355501; 631715, 3331921; 
626248, 3340616; 625625, 3345344; 627413, 3348318; 626114, 3355671; 
631471, 3332178; 626198, 3340698; 625606, 3345399; 627408, 3348352; 
626003, 3355887; 625892, 3356012; 626988, 3362872; 620852, 3370228; 
620569, 3378594; 621288, 3393373; 625696, 3356168; 627059, 3363002; 
620823, 3370453; 620428, 3378890; 621399, 3393696; 625508, 3356261; 
627048, 3363140; 620780, 3370694; 620301, 3379176; 621298, 3394037; 
625355, 3356321; 626935, 3363277; 620757, 3370844; 620111, 3379615; 
621224, 3394231; 625101, 3356406; 626752, 3363346; 620709, 3370987; 
619995, 3379798; 621028, 3394725; 624768, 3356533; 626535, 3363388; 
620627, 3371299; 619979, 3379860; 621010, 3394884; 624561, 3356631; 
626233, 3363457; 620495, 3371585; 619978, 3379859; 621036, 3395080; 
624363, 3356763; 626054, 3363507; 620378, 3371792; 619825, 3380275; 
621071, 3395337; 624178, 3356909; 625733, 3363785; 620278, 3371982; 
619722, 3380524; 621129, 3395635; 623289, 3357491; 625498, 3364058; 
620145, 3372191; 619622, 3380763; 621161, 3395797; 623183, 3357581; 
625419, 3364351; 619981, 3372403; 619476, 3380999; 621293, 3396278; 
623043, 3357713; 625326, 3364598; 619875, 3372622; 619306, 3381361; 
621317, 3396747; 622926, 3357864; 625284, 3364746; 619746, 3372895; 
619200, 3381813; 621269, 3397173; 622873, 3357988; 625196, 3364984; 
619666, 3373085; 619210, 3382109; 621169, 3397649; 622871, 3358142; 
625133, 3365222; 619627, 3373239; 619320, 3382697; 620949, 3398123; 
622939, 3358308; 625056, 3365412; 619571, 3373464; 619399, 3383092; 
620650, 3398639; 623021, 3358441; 624892, 3365693; 619510, 3373691; 
619439, 3383481; 620311, 3399041; 623156, 3358594; 624702, 3365891; 
619473, 3373845; 619429, 3383920; 620079, 3399535; 623278, 3358737; 
624479, 3366159; 619405, 3374160; 619446, 3384315; 619914, 3400102; 
623394, 3358872; 624270, 3366320; 619320, 3374490; 619446, 3384418; 
619869, 3400255; 623471, 3359052; 623992, 3366558; 619238, 3374699; 
619458, 3384433; 619861, 3400253; 623519, 3359234; 623783, 3366823; 
619193, 3374919; 619457, 3384433; 619868, 3400327; 623585, 3359441; 
623601, 3367056; 619217, 3375104; 619584, 3384957; 619640, 3400773; 
623656, 3359560; 623455, 3367325; 619330, 3375252; 619703, 3385534; 
619457, 3401105; 623736, 3359666; 623424, 3367566; 619428, 3375366; 
619716, 3385819; 619159, 3401333; 623815, 3359732; 623405, 3367878; 
619627, 3375533; 619697, 3386192; 619022, 3401608; 623953, 3359793; 
623426, 3368191; 619926, 3375707; 619586, 3386521; 619010, 3401951; 
624096, 3359832; 623453, 3368460; 620270, 3375760; 619465, 3386827; 
619068, 3402363; 624265, 3359885; 623434, 3368754; 620579, 3375734; 
619354, 3387142; 619136, 3402654; 624429, 3359965; 623365, 3368953; 
620878, 3375633; 619316, 3387603; 619216, 3403069; 624561, 3360065; 
623193, 3369273; 621013, 3375636; 619430, 3387910; 619202, 3403302; 
624688, 3360171; 623006, 3369439; 621241, 3375662; 619676, 3388248;

[[Page 10396]]

619102, 3403524; 624813, 3360280; 622714, 3369524; 621394, 3375734; 
620015, 3388518; 618845, 3404038; 624916, 3360428; 622537, 3369532; 
621577, 3375834; 620325, 3388648; 618689, 3404392; 625022, 3360637; 
622415, 3369474; 621680, 3375985; 620510, 3388889; 618562, 3404644; 
625127, 3360864; 622299, 3369355; 621730, 3376160; 620618, 3389230; 
618475, 3404916; 625212, 3361049; 622087, 3369180; 621751, 3376387; 
620587, 3389521; 618377, 3405369; 625310, 3361248; 621958, 3369111; 
621733, 3376557; 620497, 3389899; 618268, 3405697; 625477, 3361494; 
621794, 3369080; 621669, 3376808; 620235, 3390751; 618173, 3405951; 
625641, 3361732; 621614, 3369090; 621548, 3377107; 620187, 3390997; 
618057, 3406109; 625797, 3361917; 621426, 3369135; 621429, 3377306; 
620139, 3391339; 617953, 3406255; 625972, 3362087; 621296, 3369220; 
621296, 3377488; 620073, 3392336; 617726, 3406575; 626146, 3362248; 
621161, 3369334; 621148, 3377671; 620126, 3392540; 617385, 3406948; 
626376, 3362399; 621032, 3369469; 620997, 3377859; 620229, 3392667; 
617012, 3407268; 626681, 3362579; 620899, 3369670; 620828, 3378065; 
620587, 3392849; 616662, 3407512; 626868, 3362732; 620870, 3369918; 
620727, 3378266; 621055, 3393069; 616265, 3407702; 615797, 3407959; 
615575, 3408133; 615220, 3408451; 615099, 3408618; 614898, 3408768; 
614323, 3409067; 614151, 3409173; 613956, 3409448; 613905, 3409755; 
613985, 3410070; 614260, 3410409; 614554, 3410708; 614929, 3411049; 
615030, 3411332; 615017, 3411557; 614900, 3411975; 614673, 3412383; 
614255, 3412735; 613839, 3413036; 613408, 3413285; 613056, 3413584; 
612826, 3413851; 612742, 3413986; 612633, 3414255; 612561, 3414561; 
612585, 3414665; 612665, 3414729; 613011, 3414753; 613390, 3414765; 
613692, 3414792; 613947, 3414860; 614170, 3415008; 614294, 3415147; 
614425, 3415330; 614493, 3415529; 614505, 3415713; 614497, 3416029; 
614518, 3416714; 614484, 3417219; 614499, 3417547; 614497, 3418034; 
614574, 3418523; 614587, 3419005; 614539, 3419704; 614534, 3420407; 
614558, 3421386; 614592, 3421889; 614536, 3422667; 614452, 3423252; 
614362, 3424283; 614367, 3424675; 614346, 3425212; 614304, 3425633; 
614208, 3426024; 614084, 3426572; 614089, 3426810; 614071, 3426879; 
614074, 3426892; 614073, 3426892; 614073, 3427291; 614202, 3427646; 
614318, 3427812; 614662, 3428146; 614759, 3428248; 614759, 3428249; 
615011, 3428360; 615339, 3428453; 615619, 3428516; 616016, 3428582; 
616315, 3428667; 616551, 3428866; 616741, 3429104; 616887, 3429397; 
616955, 3429720; 617093, 3430154; 617241, 3430530; 617426, 3430847; 
617606, 3431085; 617768, 3431231; 618220, 3431485; 618937, 3431821; 
619265, 3432093; 619429, 3432265; 619548, 3432382; 619651, 3432384; 
619771, 3432387; 619863, 3432366; 619964, 3432342; 620040, 3432284; 
620101, 3432210; 620181, 3432104; 620265, 3432041; 620535, 3431940; 
620787, 3431845; 621041, 3431681; 621313, 3431493; 621453, 3431395; 
621631, 3431265; 621760, 3431186; 621887, 3431099; 622094, 3431032; 
622260, 3430982; 622385, 3430980; 622678, 3431022; 622948, 3431070; 
623065, 3431117; 623255, 3431289; 623334, 3431437; 623419, 3431670; 
623446, 3431757; 623530, 3431990; 623602, 3432109; 623692, 3432226; 
623811, 3432300; 623962, 3432377; 624152, 3432456; 624411, 3432472; 
624737, 3432448; 624930, 3432387; 625184, 3432321; 625406, 3432226; 
625650, 3432072; 626123, 3431776; 627070, 3431218.
    (ii) Note: Map of Unit 2, Upper Atchafalaya River Basin (Map 3), 
follows:
BILLING CODE 4310-55-P

[[Page 10397]]

[GRAPHIC] [TIFF OMITTED] TR10MR09.002

BILLING CODE 4310-55-C

[[Page 10398]]

    (8) Unit 3: Lower Atchafalaya River Basin. Iberia and St. Mary 
Parishes, Louisiana.
    (i) From USGS 1:24,000 scale digital ortho-photo quarter-
quadrangles: Belle Isle NE; Belle Isle NW; Belle Isle SE; Centerville 
SW; Delcambre SE; Ellerslie NE; Ellerslie NW; Ellerslie SE; Franklin 
NE; Franklin NW; Franklin SE; Franklin SW; Jeanerette SW; Kemper NE; 
Kemper NW; Kemper SE; Kemper SW; Morgan City NW; Morgan City SW; New 
Iberia South SE; New Iberia South SW; North Bend NE; North Bend NW; 
North Bend SE; North Bend SW; Patterson NW; Patterson SE; Patterson SW; 
Point Chevreuil NE; Weeks NE; Weeks NW; Weeks SE; Weeks SW; Louisiana. 
Land bounded by the following UTM Zone 15N, North American Datum of 
1983 (NAD83) coordinates (E, N): 669586, 3283741; 669490, 3283653; 
669463, 3283702; 669445, 3283673; 669416, 3283622; 669405, 3283616; 
669386, 3283618; 669315, 3283664; 669301, 3283673; 669290, 3283668; 
669253, 3283668; 669241, 3283674; 669261, 3283755; 669265, 3283781; 
669267, 3283889; 669268, 3283890; 669586, 3283741; 609762, 3311410; 
609778, 3311404; 609783, 3311405; 609784, 3311401; 609803, 3311403; 
609822, 3311403; 609823, 3311363; 609841, 3311319; 609855, 3311292; 
609883, 3311253; 609900, 3311233; 609904, 3311216; 609912, 3311178; 
609965, 3311193; 610038, 3311216; 610100, 3311230; 610151, 3311240; 
610163, 3311243; 610164, 3311258; 610163, 3311276; 610157, 3311298; 
610143, 3311324; 610143, 3311340; 610152, 3311352; 610172, 3311336; 
610183, 3311313; 610201, 3311296; 610219, 3311282; 610329, 3311060; 
610344, 3311044; 610358, 3311046; 610454, 3311164; 610483, 3311132; 
610516, 3311098; 610658, 3311126; 610730, 3311149; 610772, 3311057; 
610562, 3310951; 610692, 3310771; 610706, 3310769; 611074, 3310949; 
611095, 3310914; 610966, 3310846; 611086, 3310627; 611106, 3310620; 
611144, 3310623; 611185, 3310632; 611229, 3310647; 611271, 3310667; 
611334, 3310699; 611353, 3310648; 611368, 3310611; 611395, 3310550; 
611405, 3310517; 611422, 3310491; 611477, 3310500; 611522, 3310511; 
611569, 3310527; 611584, 3310532; 611596, 3310539; 611619, 3310547; 
611631, 3310577; 611629, 3310607; 611617, 3310637; 611603, 3310641; 
611592, 3310661; 611577, 3310689; 611558, 3310729; 611525, 3310761; 
611500, 3310786; 611402, 3310850; 611450, 3310891; 611506, 3310929; 
611572, 3310963; 611601, 3310945; 611608, 3310939; 611607, 3310932; 
611607, 3310918; 611614, 3310907; 611623, 3310906; 611634, 3310910; 
611636, 3310912; 611640, 3310909; 611671, 3310881; 611677, 3310868; 
611673, 3310855; 611675, 3310830; 611697, 3310819; 611700, 3310807; 
611691, 3310800; 611686, 3310800; 611680, 3310797; 611679, 3310787; 
611681, 3310778; 611688, 3310772; 611688, 3310765; 611693, 3310761; 
611699, 3310765; 611702, 3310769; 611711, 3310772; 611727, 3310782; 
611742, 3310786; 611755, 3310788; 611763, 3310780; 611766, 3310764; 
611766, 3310748; 611768, 3310735; 611812, 3310810; 611820, 3310818; 
611822, 3310819; 611828, 3310830; 611826,

3310842; 611820, 3310852; 611813, 3310861; 611812, 3310861; 611809, 
3310855; 611803, 3310842; 611787, 3310845; 611781, 3310856; 611781, 
3310873; 611791, 3310876; 611798, 3310886; 611812, 3310905; 612177, 
3310786; 612224, 3310851; 612316, 3310898; 612533, 3310460; 612595, 
3310210; 612609, 3310167; 612785, 3309826; 613052, 3309272; 613228, 
3309259; 613228, 3309167; 613374, 3309155; 613377, 3308952; 613256, 
3308971; 612968, 3307838; 613160, 3307840; 613181, 3307979; 613178, 
3307997; 613178, 3308031; 613184, 3308049; 613200, 3308064; 613211, 
3308086; 613222, 3308100; 613242, 3308099; 613260, 3308097; 613280, 
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3307973; 613350, 3307975; 613382, 3307990; 613413, 3308015; 613443, 
3308050; 613465, 3308071; 613489, 3308085; 613525, 3308101; 613554, 
3308123; 613582, 3308146; 613592, 3308168; 613592, 3308190; 613583, 
3308207; 613570, 3308221; 613552, 3308232; 613537, 3308251; 613521, 
3308272; 613514, 3308295; 613510, 3308312; 613511, 3308335; 613528, 
3308355; 613543, 3308374; 613568, 3308387; 613595, 3308396; 613630, 
3308413; 613650, 3308431; 613644, 3308455; 613637, 3308481; 613629, 
3308510; 613608, 3308554; 613588, 3308587; 613581, 3308626; 613577, 
3308657; 613585, 3308684; 613604, 3308707; 613622, 3308729; 613644, 
3308745; 613669, 3308751; 613710, 3308751; 613738, 3308749; 613753, 
3308749; 613751, 3308725; 613725, 3308729; 613689, 3308735; 613662, 
3308732; 613644, 3308722; 613631, 3308704; 613619, 3308683; 613608, 
3308649; 613606, 3308626; 613618, 3308587; 613638, 3308549; 613658, 
3308503; 613679, 3308454; 613682, 3308427; 613679, 3308404; 613660, 
3308392; 613633, 3308380; 613609, 3308373; 613570, 3308355; 613550, 
3308338; 613534, 3308311; 613542, 3308289; 613570, 3308269; 613592, 
3308254; 613612, 3308238; 613631, 3308208; 613635, 3308177; 613624, 
3308148; 613609, 3308123; 613588, 3308104; 613570, 3308089; 613548, 
3308077; 613520, 3308065; 613491, 3308051; 613473, 3308032; 613455, 
3308013; 613438, 3307993; 613420, 3307978; 613402, 3307959; 613388, 
3307943; 613363, 3307936; 613333, 3307935; 613312, 3307941; 613289, 
3307962; 613280, 3307983; 613272, 3308016; 613258, 3308045; 613245, 
3308054; 613231, 3308060; 613218, 3308050; 613213, 3308019; 613218, 
3307977; 613429, 3307823; 614212, 3308886; 614456, 3308891; 614451, 
3309046; 615053, 3309018; 615110, 3308968; 615135, 3308927; 615140, 
3308889; 615110, 3308754; 615103, 3308698; 615145, 3308695; 615218, 
3308619; 615428, 3308317; 615608, 3307984; 615623, 3307975; 615690, 
3307992; 615770, 3308015; 615961, 3308101; 616160, 3308197; 616364, 
3308280; 616425, 3308306; 616450, 3308315; 616478, 3308322; 616512, 
3308334; 616567, 3308356; 616593, 3308316; 616624, 3308282; 616648, 
3308253; 616679, 3308217; 616712, 3308168; 616795, 3308063; 616927, 
3307896; 617018, 3307777; 617024, 3307766; 617034, 3307750; 617040, 
3307728; 617037, 3307707; 617025, 3307669; 617025, 3307649; 617035, 
3307611; 617059, 3307590; 617086, 3307571; 617143, 3307546; 617175, 
3307539; 617206, 3307536; 617225, 3307550; 617251, 3307557; 617284, 
3307557; 617318, 3307558; 617359, 3307580; 617365, 3307556; 617417, 
3306097; 617417, 3306004; 617403, 3305843; 617409, 3305782; 617475, 
3305782; 617542, 3305784; 617794, 3305786; 617989, 3305795; 618069, 
3305792; 618103, 3305792; 618124, 3305782; 618146, 3305773; 618167, 
3305784; 618186, 3305797; 618222, 3305797; 618262, 3305797; 618423, 
3305799; 618569, 3305797; 618823, 3305805; 619318, 3305818; 619363, 
3305835; 619392, 3305888; 619409, 3305966; 619407, 3306025; 619399, 
3306095; 619399, 3306095; 619385, 3306138; 619363, 3306213; 619306, 
3306369; 619209, 3306648; 619170, 3306752; 619157, 3306773; 619141, 
3306790; 619067, 3306933; 618996, 3307074; 618965, 3307127; 618945, 
3307151; 618924, 3307164; 618908, 3307175; 618905, 3307299; 618907, 
3307803; 618917, 3307808; 619228, 3307594; 619266, 3307568; 619363, 
3307528; 619365, 3307422; 619710, 3307438; 619832, 3307440; 619836, 
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[[Page 10399]]


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3305889; 620795, 3305875; 620807, 3305850; 620812, 3305809; 620814, 
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3305406; 620959, 3305376; 620970, 3305347; 620980, 3305320; 620998, 
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3304841; 621034, 3304824; 621025, 3304807; 620981, 3304717; 620979, 
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3304108; 621625, 3304083; 621572, 3304050; 621135, 3303792; 621114, 
3303780; 621107, 3303756; 621107, 3303506; 621112, 3303487; 621133, 
3303475; 621481, 3303334; 621543, 3303301; 621624, 3303231; 622084, 
3302822; 622130, 3302798; 622506, 3302723; 622558, 3303109; 622618, 
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3304668; 623545, 3304680; 623547, 3304703; 623544, 3304790; 623542, 
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3305496; 623902, 3305498; 623957, 3305543; 623959, 3305338; 624063, 
3305344; 624069, 3304738; 623996, 3304738; 623974, 3304730; 623959, 
3304714; 623941, 3304702; 623912, 3304693; 623599, 3304638; 623610, 
3304305; 623976, 3304291; 623980, 3304224; 623609, 3304089; 623614, 
3304055; 623629, 3304049; 623640, 3304046; 623627, 3303808; 623630, 
3303747; 623637, 3303658; 623643, 3303610; 623643, 3303572; 623640, 
3303541; 623640, 3303513; 623650, 3303468; 623661, 3303428; 623672, 
3303410; 623691, 3303403; 623753, 3303389; 624068, 3303366; 624104, 
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3303284; 625149, 3304020; 625240, 3304221; 626172, 3304232; 626181, 
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3303647; 626116, 3303646; 626100, 3303642; 626077, 3303635; 626055, 
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3299934; 628869, 3299954; 628905, 3299976; 628971, 3300013; 629106, 
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3300028; 629635, 3300223; 629683, 3300351; 629717, 3300438; 629736, 
3300486; 629765, 3300532; 629801, 3300576; 629847, 3300613; 629894, 
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3299734; 632151, 3299752; 631884, 3299543; 631823, 3299288; 632200, 
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3298903; 632586, 3298891; 632640, 3299122; 632598, 3299143; 632546, 
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3299204; 632656, 3299168; 632695, 3299137; 632777, 3299137; 632774, 
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3298909; 632765, 3298906; 632756, 3298885; 632795, 3298779; 632853, 
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3299563; 633139, 3299572; 633205, 3299590; 633445, 3299620; 633739, 
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3299581; 634288, 3299638; 634264, 3299666; 634251, 3299720; 634245, 
3299769; 634215, 3299806; 634212, 3299848; 634239, 3299863; 634242, 
3299906; 634218, 3299954; 634188, 3300009; 634154, 3300059; 634142, 
3300120; 634151, 3300178; 634139, 3300217; 634106, 3300263; 634127, 
3300278; 634182, 3300232; 634182, 3300196; 634182, 3300172; 634428, 
3300153; 634443, 3299877; 634747, 3299925; 634728, 3300129; 634783, 
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3300323; 634945, 3300396; 635021, 3300396; 635030, 3300326; 635191, 
3300333; 635194, 3300415; 635267, 3300411; 635261, 3300497; 635364, 
3300500; 635376, 3300287; 635501, 3300296; 635549, 3298905; 635677, 
3298899; 635698, 3298981; 635738, 3299069; 635805, 3299142; 635917, 
3299196; 636066, 3299285; 636172, 3299312; 636598, 3299534; 636598, 
3299795; 636559, 3299843; 636510, 3299895; 636465, 3299953; 636440, 
3300004; 636592, 3300041; 636596, 3300661; 636669, 3300664; 636696, 
3300254; 636723, 3300245; 636741, 3300276; 636876, 3300290; 636939, 
3300303; 637011, 3299780; 637093, 3299870; 637138, 3299929; 637183, 
3299987; 637260, 3300055; 637287, 3300109; 637332, 3300109; 637381, 
3300163; 637454, 3300168; 637688, 3299848; 637905, 3299906; 638026, 
3299983; 638099, 3300015; 638139, 3300028; 638477, 3299577; 638906, 
3299947; 639351, 3299694; 639448, 3299535; 639665, 3299398; 639812, 
3299240; 640165, 3299019; 640307, 3299240; 640460, 3299198; 640734, 
3299156; 640976, 3299003; 641019, 3299056; 641240, 3298882; 641287, 
3298766; 641398, 3298297; 641487, 3297907; 641298, 3297886; 641314, 
3297781; 641293, 3297702; 641293, 3297559; 641145, 3297549; 641161, 
3297249; 640940, 3297222; 640955, 3297054; 640866, 3297038; 640855, 
3296938; 640829, 3296832; 640766, 3296722; 640760, 3296622; 640755, 
3296495; 640773, 3296405; 640871, 3296405; 640904, 3296382; 640950, 
3296394; 640957, 3296394; 640955, 3296209; 640838, 3296194; 640860, 
3296030; 640862, 3296025; 640861, 3296011; 640863, 3295984; 640879, 
3295944; 640893, 3295931; 640910, 3295907; 640963, 3295821; 640977, 
3295788; 641008, 3295737; 641018, 3295707; 641057, 3295703; 641079, 
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[[Page 10400]]

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3295525; 641858, 3295472; 641944, 3295427; 641987, 3295431; 642085, 
3295387; 642172, 3295345; 642163, 3295009; 642204, 3294820; 642262, 
3294541; 642311, 3294311; 642270, 3293802; 642377, 3293777; 642401, 
3293741; 642409, 3293673; 642471, 3293581; 642602, 3293612; 642659, 
3293702; 642664, 3293703; 642598, 3294408; 642779, 3294465; 642720, 
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3295003; 642817, 3295078; 642747, 3295127; 642873, 3295239; 642952, 
3295247; 643087, 3295317; 643253, 3295030; 643199, 3294998; 643269, 
3294815; 643382, 3294885; 643431, 3294852; 643501, 3294756; 643791, 
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3294379; 644604, 3294271; 644604, 3294126; 644523, 3294067; 644518, 
3294018; 644582, 3293954; 644539, 3293911; 644728, 3293798; 644889, 
3293986; 645077, 3293828; 645474, 3293457; 645855, 3293869; 645868, 
3293848; 645707, 3293599; 645899, 3293490; 645938, 3293538; 646083, 
3293459; 646065, 3293411; 646096, 3293358; 646192, 3293310; 646367, 
3293258; 646428, 3293252; 646227, 3292720; 646251, 3292706; 646213, 
3292643; 646335, 3292568; 646377, 3292540; 646349, 3292462; 646448, 
3292387; 646434, 3292333; 646591, 3292234; 646666, 3292380; 647115, 
3292177; 647097, 3292073; 647403, 3291977; 647435, 3292009; 647880, 
3291913; 647882, 3291917; 647943, 3291895; 647963, 3292053; 648154, 
3292006; 648159, 3292045; 648185, 3292068; 648432, 3292073; 648803, 
3291899; 648796, 3291867; 648956, 3291810; 648952, 3291756; 649013, 
3291732; 648999, 3291603; 649262, 3291557; 649301, 3291707; 649583, 
3291642; 649622, 3291803; 649739, 3291778; 649771, 3291853; 650067, 
3291646; 650121, 3291888; 650217, 3291881; 650206, 3291806; 650316, 
3291781; 650416, 3291966; 650460, 3291968; 650504, 3291933; 650318, 
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3290823; 651880, 3290648; 651865, 3290552; 651852, 3290510; 651815, 
3290312; 651921, 3290229; 651909, 3290025; 651976, 3290007; 651968, 
3289862; 652004, 3289851; 652015, 3289745; 652020, 3289613; 652320, 
3289443; 652374, 3289404; 652654, 3289394; 652899, 3289259; 652902, 
3289417; 653065, 3289313; 653182, 3289452; 653290, 3289507; 653308, 
3289572; 653398, 3289580; 653417, 3289691; 653541, 3289575; 653655, 
3289391; 653913, 3288941; 654058, 3288729; 654177, 3288607; 654976, 
3288053; 655902, 3287319; 655781, 3287248; 655615, 3287375; 655513, 
3287321; 655674, 3287185; 655484, 3287102; 655254, 3287326; 655171, 
3287282; 655210, 3287234; 655059, 3287155; 655152, 3286936; 654722, 
3286711; 654790, 3286633; 655078, 3286750; 655103, 3286658; 654995, 
3286619; 655034, 3286550; 655952, 3286902; 655976, 3286824; 656001, 
3286746; 656040, 3286706; 656055, 3286628; 656055, 3286560; 656059, 
3286511; 656147, 3286404; 656016, 3286277; 655908, 3286179; 655815, 
3286067; 655723, 3285935; 655654, 3285886; 655884, 3285750; 655869, 
3285730; 656045, 3285550; 655708, 3285140; 655703, 3285047; 656035, 
3285081; 656167, 3285296; 656196, 3285286; 656509, 3285164; 656665, 
3285516; 656401, 3285638; 656716, 3286097; 656751, 3286102; 656774, 
3286166; 656877, 3286373; 657008, 3286623; 657184, 3286570; 657366, 
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3286418; 657683, 3286414; 657764, 3286398; 657883, 3286379; 658022, 
3286368; 658206, 3286356; 658438, 3286343; 658583, 3286337; 658759, 
3286325; 658976, 3286296; 659151, 3286268; 659787, 3286180; 659778, 
3286078; 659788, 3286043; 659692, 3285983; 659656, 3285856; 659673, 
3285837; 659807, 3285818; 659775, 3285720; 659833, 3285706; 660163, 
3285649; 660175, 3285669; 660188, 3285753; 660209, 3285754; 660209, 
3285604; 660223, 3285599; 660236, 3285542; 660251, 3285544; 660252, 
3285562; 660452, 3285536; 660450, 3285803; 660491, 3285800; 660492, 
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3285511; 662816, 3285502; 662836, 3285493; 662844, 3285471; 662838, 
3285460; 662840, 3285427; 662838, 3285403; 662842, 3285385; 662886, 
3285304; 662752, 3285220; 662735, 3285244; 662739, 3285271; 662724, 
3285273; 662686, 3285258; 662611, 3285385; 662770, 3285484; 662774, 
3285500; 662719, 3285583; 662587, 3285513; 662565, 3285376; 662466, 
3285403; 662479, 3285363; 662620, 3285124; 662374, 3284950; 662358, 
3285000; 662358, 3285016; 662323, 3285069; 662310, 3285069; 662281, 
3285058; 662306, 3284998; 662290, 3284972; 662312, 3284945; 662341, 
3284912; 662253, 3284846; 662301, 3284747; 662411, 3284816; 662473, 
3284706; 662515, 3284728; 662598, 3284620; 662895, 3284827; 663003, 
3284670; 663139, 3284767; 663229, 3284651; 662671, 3284215; 662622, 
3284178; 662587, 3284154; 662550, 3284198; 662383, 3284068; 662420, 
3284011; 662455, 3283993; 662486, 3283973; 662526, 3283986; 662583, 
3284013; 662649, 3284077; 662732, 3284006; 663207, 3284391; 663342, 
3284266; 663474, 3284376; 663670, 3284338; 664075, 3284719; 664163, 
3284618; 663921, 3284279; 664013, 3284252; 663941, 3284180; 663870, 
3284149; 663791, 3284132; 663727, 3284136; 663683, 3284143; 663615, 
3284158; 663562, 3284169; 663479, 3284191; 663098, 3283840; 663298, 
3283619; 663322, 3283640; 663345, 3283712; 663231, 3283834; 663506, 
3284083; 663538, 3284076; 663583, 3284066; 663642, 3284055; 663653, 
3284087; 663672, 3284127; 663736, 3284116; 663798, 3284116; 663851, 
3284123; 663903, 3284140; 663945, 3284162; 664037, 3284255; 664218, 
3284206; 663826, 3283777; 663694, 3283901; 663296, 3283362; 663391, 
3283262; 663301, 3283141; 663411, 3283006; 663870, 3283512; 663914, 
3283477; 663956, 3283523; 663996, 3283488; 663763, 3283224; 663785, 
3283200; 663800, 3283176; 663822, 3283174; 663855, 3283180; 663857, 
3283209; 663844, 3283240; 663829, 3283270; 663923, 3283385; 664103, 
3283204; 664152, 3283253; 664194, 3283213; 664229, 3283156; 664211, 
3283070; 664191, 3283035; 664163, 3282984; 664174, 3282965; 664224, 
3282973; 664286, 3282976; 664355, 3282956; 664393, 3283028; 664511, 
3283006; 664536, 3283061; 664591, 3283035; 664615, 3283020; 664654, 
3282953; 664663, 3282913; 664608, 3282658; 664573, 3282565; 664549, 
3282535; 664553, 3282519; 664595, 3282532; 664624, 3282614; 664652, 
3282697; 664661, 3282748; 664661, 3282794; 664661, 3282840; 664674, 
3282882; 664698, 3282968; 664881, 3282906; 664828, 3282660; 664791, 
3282535; 664723, 3282486; 664692, 3282475; 664643, 3282486; 664613, 
3282405; 664582, 3282343; 664577, 3282299; 664569, 3282262; 664575, 
3282195; 664582, 3282153; 664586, 3282100; 664562, 3282030; 664544, 
3281973; 664591, 3281940; 664676, 3281916; 664751, 3281900; 664771, 
3281896; 664789, 3281944; 664806, 3281962; 664852, 3282001; 664894, 
3282041; 664907, 3282129; 664907, 3282204; 664921, 3282278; 664960,

[[Page 10401]]

3282300; 665044, 3282287; 665068, 3282294; 665066, 3282355; 665092, 
3282388; 665112, 3282424; 665119, 3282468; 665114, 3282509; 665209, 
3283174; 665314, 3284000; 665286, 3284004; 665317, 3284226; 665418, 
3284215; 665438, 3284310; 665616, 3284282; 665752, 3284277; 665759, 
3284243; 665754, 3284206; 665745, 3284087; 665704, 3283858; 665734, 
3283845; 665804, 3283853; 665873, 3283866; 665938, 3283880; 665972, 
3283877; 666015, 3283880; 666033, 3283875; 666039, 3283830; 666087, 
3283835; 666087, 3283900; 666128, 3283908; 666279, 3283937; 666269, 
3283987; 666252, 3284006; 666250, 3284038; 666248, 3284061; 666246, 
3284091; 666239, 3284139; 666228, 3284184; 666220, 3284228; 666237, 
3284232; 666251, 3284177; 666255, 3284147; 666265, 3284120; 666277, 
3284104; 666286, 3284099; 666327, 3283914; 666351, 3283841; 666395, 
3283791; 666593, 3283884; 666600, 3283871; 666410, 3283777; 666431, 
3283753; 666543, 3283813; 666560, 3283782; 666535, 3283757; 666549, 
3283724; 666509, 3283703; 666500, 3283713; 666522, 3283732; 666512, 
3283743; 666458, 3283710; 666509, 3283615; 666546, 3283593; 666583, 
3283594; 666625, 3283605; 666691, 3283622; 666738, 3283639; 666770, 
3283649; 666936, 3283820; 666930, 3283852; 666786, 3283796; 666910, 
3283894; 666855, 3284022; 667079, 3284061; 667059, 3284132; 666821, 
3284080; 666727, 3284242; 666691, 3284320; 666700, 3284326; 666824, 
3284099; 666850, 3284115; 666744, 3284293; 666760, 3284299; 666870, 
3284108; 666896, 3284121; 666754, 3284357; 666761, 3284368; 666916, 
3284121; 666960, 3284132; 666959, 3284141; 666797, 3284402; 666808, 
3284404; 666977, 3284137; 666992, 3284144; 666996, 3284150; 666900, 
3284297; 666909, 3284302; 667016, 3284143; 667028, 3284144; 667039, 
3284148; 666910, 3284340; 666923, 3284343; 667047, 3284172; 667095, 
3284254; 667131, 3284331; 667111, 3284345; 667188, 3284455; 667227, 
3284479; 667264, 3284537; 667389, 3284572; 667390, 3284597; 667639, 
3284656; 667634, 3284709; 668470, 3284932; 669015, 3285050; 669035, 
3284975; 669054, 3284945; 669115, 3284724; 669239, 3284764; 669144, 
3285070; 669046, 3285049; 669025, 3285064; 669023, 3285088; 668973, 
3285200; 669273, 3285296; 669544, 3285373; 669649, 3285399; 670426, 
3285579; 671128, 3285751; 671141, 3285754; 671173, 3285652; 671415, 
3285708; 671513, 3285733; 671511, 3285792; 671613, 3285799; 671718, 
3285729; 671673, 3285714; 671780, 3285641; 671802, 3285574; 671933, 
3285608; 671962, 3285587; 672018, 3285482; 671936, 3285360; 671936, 
3285358; 671928, 3285353; 671892, 3285319; 671865, 3285381; 671610, 
3285301; 671664, 3285268; 671738, 3285301; 671732, 3285261; 671750, 
3285261; 671761, 3285278; 671828, 3285280; 671850, 3285250; 671857, 
3285224; 671869, 3285167; 671773, 3285022; 671906, 3284961; 671877, 
3284901; 671729, 3284955; 671689, 3284894; 671571, 3284724; 671664, 
3284692; 671653, 3284660; 671596, 3284672; 671574, 3284670; 671542, 
3284682; 671402, 3284479; 671595, 3284403; 671525, 3284348; 671467, 
3284370; 671397, 3284397; 671347, 3284400; 671362, 3284380; 671342, 
3284294; 671377, 3284247; 671319, 3284214; 671180, 3284123; 671131, 
3284070; 671123, 3284063; 671102, 3284084; 671061, 3284147; 671038, 
3284179; 671007, 3284171; 671032, 3284107; 671051, 3284057; 671057, 
3284013; 670928, 3283945; 670697, 3283651; 670674, 3283618; 670612, 
3283650; 670548, 3283560; 670525, 3283558; 670505, 3283541; 670479, 
3283497; 670385, 3283308; 670349, 3283331; 670318, 3283301; 670054, 
3282799; 670019, 3282786; 670003, 3283123; 670002, 3283122; 670001, 
3283277; 669969, 3283284; 669951, 3283293; 669915, 3283295; 669892, 
3283287; 669876, 3283283; 669859, 3283302; 669807, 3283290; 669772, 
3283285; 669751, 3283285; 669729, 3283287; 669722, 3283278; 669722, 
3283260; 669738, 3283235; 669734, 3283223; 669727, 3283211; 669726, 
3283191; 669736, 3283181; 669752, 3283171; 669773, 3283176; 669784, 
3283185; 669804, 3283183; 669818, 3283174; 669829, 3283160; 669835, 
3283144; 669844, 3283119; 669849, 3283099; 669851, 3283079; 669853, 
3283052; 669854, 3283044; 669830, 3283030; 669814, 3283005; 669829, 
3282983; 669842, 3282945; 669840, 3282938; 669829, 3282933; 669822, 
3282925; 669811, 3282925; 669800, 3282923; 669784, 3282919; 669772, 
3282923; 669761, 3282931; 669756, 3282936; 669742, 3282943; 669736, 
3282954; 669739, 3282960; 669740, 3282969; 669730, 3282975; 669722, 
3282981; 669726, 3282991; 669730, 3283006; 669729, 3283018; 669718, 
3283013; 669713, 3283023; 669712, 3283035; 669711, 3283047; 669718, 
3283057; 669720, 3283068; 669713, 3283071; 669700, 3283069; 669695, 
3283065; 669675, 3283077; 669672, 3283075; 669654, 3283075; 669647, 
3283079; 669644, 3283092; 669629, 3283091; 669622, 3283088; 669616, 
3283081; 669608, 3283077; 669594, 3283076; 669580, 3283082; 669565, 
3283095; 669562, 3283084; 669561, 3283072; 669554, 3283067; 669547, 
3283062; 669541, 3283047; 669530, 3283045; 669520, 3283053; 669511, 
3283048; 669497, 3283055; 669493, 3283060; 669485, 3283062; 669478, 
3283060; 669463, 3283058; 669453, 3283067; 669447, 3283071; 669436, 
3283071; 669432, 3283077; 669434, 3283086; 669436, 3283097; 669437, 
3283106; 669432, 3283113; 669425, 3283115; 669419, 3283121; 669419, 
3283135; 669420, 3283143; 669418, 3283158; 669417, 3283161; 669421, 
3283180; 669472, 3283179; 669423, 3283234; 669418, 3283249; 669402, 
3283259; 669407, 3283276; 669377, 3283276; 669375, 3283296; 669375, 
3283304; 669379, 3283317; 669376, 3283330; 669376, 3283342; 669379, 
3283355; 669380, 3283365; 669374, 3283378; 669370, 3283389; 669377, 
3283403; 669385, 3283408; 669396, 3283420; 669409, 3283428; 669415, 
3283429; 669421, 3283437; 669437, 3283440; 669444, 3283448; 669453, 
3283451; 669461, 3283455; 669461, 3283459; 669472, 3283468; 669469, 
3283481; 669463, 3283488; 669491, 3283510; 669489, 3283521; 669493, 
3283529; 669505, 3283533; 669518, 3283543; 669530, 3283550; 669531, 
3283564; 669546, 3283570; 669552, 3283579; 669559, 3283586; 669568, 
3283593; 669570, 3283595; 669585, 3283590; 669597, 3283596; 669609, 
3283590; 669619, 3283580; 669628, 3283567; 669641, 3283565; 669656, 
3283556; 669661, 3283547; 669663, 3283535; 669675, 3283537; 669685, 
3283552; 669677, 3283565; 669684, 3283573; 669692, 3283579; 669691, 
3283590; 669685, 3283598; 669675, 3283605; 669667, 3283606; 669667, 
3283616; 669648, 3283617; 669639, 3283616; 669640, 3283603; 669626, 
3283600; 669607, 3283607; 669599, 3283616; 669594, 3283619; 669605, 
3283630; 669627, 3283649; 669640, 3283668; 669650, 3283678; 669658, 
3283670; 669665, 3283655; 669668, 3283639; 669675, 3283630; 669680, 
3283623; 669685, 3283613; 669688, 3283612; 669697, 3283605; 669708, 
3283596; 669716, 3283584; 669712, 3283569; 669706, 3283556; 669683, 
3283536; 669691, 3283526; 669704, 3283512; 669705, 3283493; 669687, 
3283490; 669675, 3283492; 669663, 3283497; 669661, 3283486; 669668, 
3283473; 669681, 3283461; 669685, 3283453; 669693, 3283448; 669705,

3283445; 669709, 3283437; 669709, 3283426; 669709, 3283417; 669717, 
3283410; 669729, 3283403; 669743, 3283400; 669749, 3283405; 669764,

[[Page 10402]]

3283410; 669772, 3283398; 669776, 3283387; 669781, 3283372; 669793, 
3283368; 669792, 3283353; 669798, 3283343; 669797, 3283326; 669798, 
3283308; 669809, 3283298; 669840, 3283308; 669873, 3283317; 669902, 
3283319; 669930, 3283320; 669950, 3283317; 669975, 3283316; 670000, 
3283331; 669996, 3283450; 670162, 3283622; 669911, 3283896; 669884, 
3283886; 669873, 3283879; 669872, 3283860; 669875, 3283843; 669869, 
3283832; 669858, 3283838; 669847, 3283837; 669840, 3283828; 669824, 
3283823; 669812, 3283832; 669798, 3283836; 669791, 3283826; 669798, 
3283812; 669808, 3283798; 669826, 3283780; 669823, 3283769; 669809, 
3283764; 669799, 3283779; 669789, 3283793; 669780, 3283787; 669780, 
3283776; 669783, 3283757; 669788, 3283744; 669801, 3283731; 669816, 
3283725; 669828, 3283728; 669838, 3283726; 669835, 3283734; 669842, 
3283744; 669850, 3283740; 669861, 3283728; 669870, 3283718; 669884, 
3283712; 669896, 3283703; 669903, 3283697; 669919, 3283705; 669926, 
3283696; 669922, 3283683; 669908, 3283679; 669903, 3283670; 669886, 
3283669; 669874, 3283686; 669857, 3283701; 669841, 3283705; 669829, 
3283698; 669825, 3283707; 669804, 3283709; 669783, 3283721; 669772, 
3283735; 669764, 3283757; 669759, 3283773; 669761, 3283792; 669767, 
3283800; 669770, 3283816; 669768, 3283832; 669782, 3283857; 669784, 
3283873; 669770, 3283885; 669788, 3283902; 669840, 3283942; 669856, 
3283955; 669901, 3284004; 669902, 3283998; 670788, 3284599; 670852, 
3284650; 670859, 3284783; 670879, 3284846; 670888, 3284880; 670900, 
3284899; 670986, 3285078; 671023, 3285026; 671045, 3285002; 671052, 
3284928; 671056, 3284888; 671187, 3285043; 671108, 3285061; 671030, 
3285098; 670971, 3285125; 670852, 3284884; 670761, 3284884; 670625, 
3284870; 670623, 3284717; 670366, 3284677; 670358, 3284969; 670299, 
3285015; 669927, 3284914; 669684, 3284485; 669646, 3284485; 669270, 
3284388; 669230, 3284001; 669122, 3284303; 668785, 3284234; 668790, 
3284204; 668781, 3284180; 668759, 3284163; 668736, 3284130; 668759, 
3284116; 668785, 3284113; 668809, 3284111; 668812, 3284096; 668805, 
3284070; 668821, 3284049; 668835, 3284037; 668836, 3284002; 668835, 
3283963; 668826, 3283932; 668819, 3283903; 668786, 3283897; 668771, 
3283916; 668759, 3283899; 668774, 3283870; 668771, 3283854; 668745, 
3283858; 668709, 3283877; 668697, 3283885; 668683, 3283877; 668679, 
3283839; 668700, 3283809; 668697, 3283787; 668707, 3283766; 668667, 
3283763; 668636, 3283794; 668633, 3283828; 668612, 3283830; 668579, 
3283799; 668566, 3283778; 668564, 3283742; 668562, 3283708; 668550, 
3283685; 668512, 3283654; 668495, 3283639; 668474, 3283604; 668462, 
3283580; 668426, 3283604; 668423, 3283632; 668400, 3283628; 668393, 
3283649; 668397, 3283692; 668407, 3283727; 668421, 3283742; 668424, 
3283775; 668461, 3283796; 668495, 3283796; 668540, 3283822; 668569, 
3283828; 668617, 3283856; 668633, 3283884; 668654, 3283909; 668673, 
3283928; 668676, 3283951; 668686, 3283982; 668697, 3284015; 668716, 
3284030; 668719, 3284054; 668692, 3284087; 668681, 3284104; 668652, 
3284123; 668628, 3284130; 668607, 3284152; 668594, 3284196; 668307, 
3284137; 668292, 3284113; 668343, 3284072; 668338, 3284054; 668326, 
3284039; 668324, 3284009; 668315, 3283983; 668299, 3283957; 668254, 
3284047; 668253, 3284046; 668238, 3284083; 668219, 3284112; 668208, 
3284127; 668193, 3284154; 668181, 3284168; 668162, 3284149; 668142, 
3284144; 668141, 3284134; 668165, 3284078; 668182, 3284076; 668203, 
3284081; 668214, 3284072; 668215, 3284053; 668222, 3284051; 68237, 
3284030; 668204, 3284022; 668194, 3284033; 668115, 3283994; 668139, 
3283945; 668121, 3283941; 668110, 3283954; 668049, 3283916; 668007, 
3283886; 667961, 3283850; 667949, 3283831; 667943, 3283809; 667922, 
3283779; 667897, 3283757; 667870, 3283725; 667844, 3283708; 667814, 
3283688; 667774, 3283666; 667754, 3283650; 667736, 3283630; 667714, 
3283609; 667694, 3283589; 667676, 3283562; 667658, 3283545; 667635, 
3283530; 667622, 3283511; 667585, 3283476; 667562, 3283460; 667497, 
3283403; 667444, 3283355; 667417, 3283334; 667382, 3283351; 667368, 
3283368; 667346, 3283391; 667338, 3283408; 667329, 3283416; 667278, 
3283391; 667265, 3283382; 667257, 3283361; 667296, 3283341; 667292, 
3283330; 667305, 3283324; 667319, 3283324; 667339, 3283331; 667354, 
3283332; 667372, 3283329; 667395, 3283316; 667351, 3283248; 667328, 
3283246; 667281, 3283193; 667254, 3283205; 667191, 3283135; 667301, 
3283072; 667360, 3283004; 667297, 3282958; 667285, 3282907; 667189, 
3282924; 667143, 3282827; 667052, 3282753; 666955, 3282679; 666932, 
3282633; 666841, 3282639; 666414, 3282189; 666425, 3281372; 666423, 
3281355; 666440, 3281311; 666628, 3281439; 666807, 3281566; 666838, 
3281588; 666890, 3281638; 666945, 3281684; 666994, 3281718; 667035, 
3281765; 667096, 3281813; 667137, 3281837; 667188, 3281865; 667263, 
3281898; 667339, 3281920; 667400, 3281932; 667465, 3281949; 667524, 
3281961; 667592, 3281954; 667632, 3281950; 667688, 3281927; 667742, 
3281918; 667800, 3281930; 667882, 3281952; 667924, 3281967; 667873, 
3282153; 668024, 3282160; 668043, 3282102; 668152, 3282117; 668112, 
3282232; 668060, 3282243; 668181, 3282333; 668279, 3282387; 668390, 
3282209; 668427, 3282209; 668461, 3282231; 668466, 3282259; 668446, 
3282274; 668417, 3282297; 668390, 3282328; 668380, 3282353; 668368, 
3282382; 668363, 3282408; 668352, 3282415; 668342, 3282425; 668354, 
3282432; 668366, 3282452; 668373, 3282472; 668371, 3282489; 668376, 
3282503; 668402, 3282500; 668395, 3282469; 668390, 3282449; 668385, 
3282421; 668383, 3282391; 668402, 3282365; 668404, 3282347; 668421, 
3282326; 668451, 3282297; 668483, 3282274; 668575, 3282234; 668575, 
3282234; 668544, 3282178; 668517, 3282156; 668512, 3282130; 668525, 
3282060; 668536, 3282016; 668543, 3281983; 668485, 3281959; 668425, 
3281941; 668337, 3281916; 668252, 3281883; 668203, 3281871; 668163, 
3281863; 668112, 3281840; 668024, 3281814; 667948, 3281789; 667778, 
3281733; 667769, 3281733; 667707, 3281740; 667585, 3281765; 667565, 
3281774; 667544, 3281774; 667469, 3281763; 667416, 3281756; 667331, 
3281732; 667237, 3281700; 667208, 3281691; 667165, 3281671; 667039, 
3281594; 666961, 3281549; 666870, 3281484; 666781, 3281425; 666750, 
3281400; 666712, 3281376; 666666, 3281352; 666547, 3281261; 666463, 
3281212; 666347, 3281131; 666350, 3281130; 666338, 3281123; 666314, 
328111; 666298, 3281096; 666268, 3281078; 666249, 3281065; 666224, 
3281051; 666199, 3281036; 666182, 3281028; 666151, 3281019; 666124, 
3281017; 666094, 3281018; 666059, 3281016; 666004, 3281017; 665971, 
3281017; 665933, 3281014; 665883, 3281016; 665844, 3281014; 665780, 
3281016; 665661, 3281017; 665658, 3281048; 665677, 3281053; 665697, 
3281062; 665723, 3281065; 665741, 3281058; 665758, 3281060; 665755, 
3281073; 665737, 3281078; 665718, 3281078; 665701, 3281080; 665675, 
3281089; 665669, 3281096; 665670, 3281117; 665592, 3281117; 665592, 
3281107; 665577, 3281093; 665564, 3281081; 665580, 3281009; 665567, 
3281005; 665541, 3281007; 665519, 3281005; 665466, 3280990; 665395,

[[Page 10403]]

3280977; 665348, 3280960; 665314, 3280949; 665300, 3280930; 665281, 
3280929; 665249, 3281049; 665212, 3281036; 665247, 3280927; 665195, 
3280912; 665163, 3280904; 665135, 3280896; 665092, 3280885; 665034, 
3280871; 664995, 3280858; 664951, 3280846; 664902, 3280832; 664864, 
3280817; 664835, 3280810; 664799, 3280796; 664756, 3280785; 664706, 
3280771; 664646, 3280753; 664603, 3280741; 664550, 3280719; 664499, 
3280705; 664458, 3280693; 664428, 3280681; 664382, 3280670; 664341, 
3280656; 664286, 3280645; 664248, 3280628; 664177, 3280610; 664111, 
3280591; 664055, 3280573; 663981, 3280553; 663933, 3280538; 663871, 
3280516; 663813, 3280497; 663760, 3280482; 663704, 3280465; 663681, 
3280458; 663622, 3280438; 663559, 3280426; 663485, 3280402; 663434, 
3280385; 663382, 3280374; 663329, 3280365; 663290, 3280360; 663238, 
3280350; 663190, 3280337; 663144, 3280328; 663122, 3280320; 663081, 
3280308; 663048, 3280301; 663007, 3280294; 662962, 3280291; 662904, 
3280290; 662865, 3280290; 662818, 3280288; 662787, 3280290; 662751, 
3280291; 662726, 3280293; 662687, 3280292; 662643, 3280287; 662631, 
3280289; 662624, 3280397; 662594, 3280398; 662567, 3280390; 662549, 
3280388; 662518, 3280393; 662519, 3280291; 662496, 3280291; 62465, 
3280290; 662442, 3280287; 662400, 3280285; 662361, 3280287; 662310, 
3280287; 662283, 3280287; 662283, 3280285; 662265, 3280287; 662194, 
3280291; 662139, 3280299; 662101, 3280300; 661966, 3280308; 661929, 
3280308; 661867, 3280308; 661819, 3280316; 661768, 3280316; 661697, 
3280317; 661629, 3280321; 661569, 3280322; 661313, 3280340; 661194, 
3280346; 661069, 3280357; 660939, 3280362; 660734, 3280381; 660551, 
3280396; 660479, 3280405; 660250, 3280098; 660146, 3280108; 660090, 
3280120; 660076, 3280116; 660029, 3280115; 660008, 3280128; 659988, 
3280129; 659950, 3280132; 659898, 3280110; 659870, 3280110; 659851, 
3280119; 659833, 3280126; 659777, 3280123; 659756, 3280135; 659718, 
3280135; 659690, 3280139; 659671, 3280152; 659637, 3280154; 659594, 
3280144; 659558, 3280145; 659519, 3280138; 659497, 3280145; 659470, 
3280152; 659423, 3280157; 659400, 3280166; 659358, 3280168; 659323, 
3280171; 659272, 3280170; 659249, 3280173; 659226, 3280166; 659217, 
3280138; 659204, 3280076; 659201, 3280045; 659204, 3280009; 659211, 
3279968; 659253, 3279817; 659407, 3279219; 659423, 3279156; 659445, 
3279082; 659402, 3279053; 659353, 3279024; 659312, 3279011; 659295, 
3278994; 659284, 3278969; 659283, 3278952; 659272, 3278924; 659252, 
3278927; 659230, 3278949; 659205, 3278968; 659179, 3278974; 659160, 
3278971; 659136, 3278951; 659122, 3278929; 659100, 3278912; 659081, 
3278904; 659063, 3278915; 659041, 3278940; 659008, 3278969; 658977, 
3278975; 658956, 3278975; 658932, 3278952; 658928, 3278938; 658923, 
3278917; 658922, 3278895; 658911, 3278872; 658900, 3278856; 658891, 
3278836; 658884, 3278816; 658878, 3278796; 658878, 3278777; 658877, 
3278763; 658884, 3278738; 658889, 3278703; 658891, 3278693; 658878, 
3278675; 658858, 3278662; 658832, 3278639; 658813, 3278623; 658785, 
3278617; 658770, 3278617; 658756, 3278634; 658751, 3278656; 658740, 
3278676; 658729, 3278698; 658718, 3278716; 658706, 3278732; 658697, 
3278741; 658673, 3278746; 658652, 3278749; 658625, 3278741; 58602, 
3278726; 658577, 3278698; 658570, 3278672; 658562, 3278644; 658566, 
3278620; 658565, 3278605; 658556, 3278586; 658532, 3278582; 658503, 
3278569; 658483, 3278558; 658435, 3278537; 658404, 3278526; 658365, 
3278510; 658331, 3278506; 658298, 3278506; 658267, 3278507; 658241, 
3278507; 658211, 3278507; 658187, 3278499; 658177, 3278495; 658154, 
3278484; 658131, 3278470; 658112, 3278462; 658090, 3278448; 658076, 
3278430; 658053, 3278411; 658038, 3278383; 658025, 3278354; 658008, 
3278318; 657985, 3278279; 657979, 3278256; 657968, 3278217; 657957, 
3278183; 657955, 3278161; 657948, 3278126; 657943, 3278101; 657937, 
3278062; 657935, 3278031; 657929, 3278005; 657928, 3277978; 657921, 
3277950; 657914, 3277936; 657903, 3277905; 657890, 3277881; 657883, 
3277865; 657861, 3277837; 657844, 3277814; 657822, 3277788; 657794, 
3277753; 657771, 3277715; 657749, 3277674; 657731, 3277645; 657703, 
3277600; 657689, 3277570; 657666, 3277519; 657652, 3277482; 657641, 
3277429; 657631, 3277366; 657624, 3277296; 657619, 3277237; 657622, 
3277197; 657630, 3277133; 657636, 3277073; 657634, 3277015; 657630, 
3276970; 657619, 3276942; 657605, 3276925; 657579, 3276924; 657565, 
3276939; 657549, 3276967; 657545, 3276998; 657548, 3277035; 657551, 
3277091; 657549, 3277122; 657555, 3277160; 657557, 3277191; 657568, 
3277232; 657568, 3277265; 657563, 3277294; 657552, 3277341; 657546, 
3277381; 657523, 3277423; 657493, 3277465; 657469, 3277491; 657433, 
3277522; 657393, 3277541; 657360, 3277550; 657320, 3277561; 657287, 
3277574; 657264, 3277581; 657236, 3277586; 657206, 3277594; 657163, 
3277608; 657115, 3277620; 657064, 3277626; 657025, 3277631; 656992, 
3277634; 656960, 3277634; 656921, 3277625; 656892, 3277619; 656856, 
3277597; 656822, 3277569; 656800, 3277539; 656772, 3277501; 656761, 
3277468; 656752, 3277439; 656743, 3277409; 656733, 3277375; 656727, 
3277329; 656724, 3277274; 656729, 3277237; 656751, 3277186; 56780, 
3277144; 656833, 3277115; 656867, 3277091; 656907, 3277091; 656952, 
3277084; 657000, 3277088; 657059, 3277087; 657115, 3277085; 657162, 
3277079; 657217, 3277059; 657267, 3277029; 657300, 3276994; 657335, 
3276955; 657354, 3276925; 657363, 3276870; 657372, 3276775; 657372, 
3276730; 657367, 3276671; 657353, 3276636; 657349, 3276608; 657339, 
3276588; 657318, 3276575; 657293, 3276563; 657275, 3276542; 657249, 
3276538; 657220, 3276542; 657196, 3276389; 657195, 3276360; 657179, 
3276334; 657165, 3276310; 657144, 3276283; 657111, 3276264; 657088, 
3276250; 657054, 3276233; 657021, 3276212; 656972, 3276191; 656954, 
3276182; 656930, 3276165; 656892, 3276147; 656861, 3276129; 656833, 
3276119; 656801, 3276099; 656771, 3276085; 656745, 3276064; 656723, 
3276039; 656695, 3276009; 656672, 3275992; 656651, 3275964; 656644, 
3275934; 656632, 3275902; 656626, 3275875; 656633, 3275844; 656640, 
3275802; 656653, 3275770; 656670, 3275751; 656694, 3275737; 656728, 
3275720; 656759, 3275715; 656803, 3275709; 656841, 3275708; 656884, 
3275709; 656939, 3275715; 656984, 3275726; 657016, 3275730; 657055, 
3275740; 657095, 3275742; 657159, 3275749; 657190, 3275750; 657215, 
3275750; 657241, 3275747; 657278, 3275733; 657303, 3275715; 657312, 
3275693; 657326, 3275664; 657335, 3275637; 657341, 3275608; 657342, 
3275564; 657352, 3275511; 657352, 3275469; 657354, 3275437; 657363, 
3275402; 657371, 3275363; 657377, 3275335; 657397, 3275305; 657407, 
3275271; 657418, 3275251; 657431, 3275230; 657457, 3275207; 657504, 
3275185; 657535, 3275167; 657582, 3275164; 657612, 3275166; 657646, 
3275173; 657675, 3275188; 657684, 3275197; 657705, 3275173; 657720, 
3275141; 657727, 3275112; 657729, 3275098; 657729, 3275084; 657714, 
3275072; 657702, 3275059; 657694, 3275048; 657695, 3275035; 657719, 
3275019; 657731, 3275029; 657744, 3275019; 657759, 3275002; 657777,

[[Page 10404]]

3274990; 657801, 3274990; 657821, 3275013; 657836, 3275032; 657855, 
3275050; 657870, 3275057; 657886, 3275052; 657900, 3275034; 657922, 
3275009; 657940, 3274994; 657954, 3274980; 657964, 3274963; 657979, 
3274955; 657989, 3274950; 658001, 3274941; 658011, 3274939; 658015, 
3274931; 658013, 3274920; 658016, 3274913; 658021, 3274906; 658028, 
3274901; 658036, 3274893; 658038, 3274881; 658042, 3274869; 658049, 
3274847; 658058, 3274835; 658052, 3274825; 658055, 3274816; 658064, 
3274805; 658070, 3274793; 658073, 3274782; 658076, 3274772; 658075, 
3274756; 658078, 3274742; 658076, 3274732; 658071, 3274725; 658074, 
3274714; 658077, 3274704; 658068, 3274699; 658056, 3274699; 658043, 
3274693; 658043, 3274681; 658054, 3274672; 658057, 3274663; 658061, 
3274654; 658058, 3274645; 658069, 3274637; 658085, 3274635; 658089, 
3274627; 658084, 3274620; 658074, 3274614; 658070, 3274605; 658075, 
3274595; 658081, 3274585; 658088, 3274579; 658093, 3274571; 658095, 
3274561; 658095, 3274549; 658084, 3274540; 658077, 3274529; 658068, 
3274526; 658055, 3274526; 658045, 3274526; 658037, 3274526; 658031, 
3274521; 658023, 3274515; 658017, 3274506; 658008, 3274496; 657999, 
3274487; 657989, 3274483; 657979, 3274482; 657976, 3274479; 657967, 
3274483; 657959, 3274485; 657952, 3274487; 657941, 3274489; 657930, 
3274487; 657928, 3274477; 657923, 3274472; 657914, 3274472; 657903, 
3274480; 657891, 3274488; 657879, 3274504; 657877, 3274519; 657861, 
3274524; 657848, 3274525; 657833, 3274526; 657815, 3274529; 657800, 
3274531; 657790, 3274535; 657779, 3274536; 657759, 3274537; 657752, 
3274536; 657729, 3274536; 657716, 3274532; 657705, 3274536; 657692, 
3274538; 657679, 3274541; 657668, 3274541; 657647, 3274537; 657629, 
3274538; 657616, 3274536; 657599, 3274529; 657593, 3274521; 657591, 
3274516; 657581, 3274515; 657569, 3274512; 657558, 3274511; 657550, 
3274516; 657545, 3274524; 657536, 3274530; 657528, 3274538; 657520, 
3274545; 657515, 3274551; 657517, 3274559; 657522, 3274563; 657525, 
3274569; 657527, 3274581; 657525, 3274590; 657518, 3274597; 657506, 
3274605; 657496, 3274610; 657493, 3274617; 657493, 3274627; 657498, 
3274636; 657499, 3274642; 657499, 3274650; 657506, 3274659; 657510, 
3274663; 657501, 3274669; 657483, 3274675; 657474, 3274683; 657465, 
3274688; 657454, 3274686; 657441, 3274686; 657423, 3274682; 657413, 
3274674; 657403, 3274664; 657398, 3274654; 657389, 3274646; 657379, 
3274645; 657364, 3274647; 657355, 3274648; 657343, 3274655; 657332, 
3274657; 657318, 3274665; 657305, 3274675; 657294, 3274686; 657277, 
3274691; 657264, 3274692; 657235, 3274692; 657220, 3274692; 657211, 
3274692; 657200, 3274694; 657196, 3274701; 657186, 3274709; 657179, 
3274711; 657166, 3274712; 657157, 3274714; 657146, 3274713; 657140, 
3274711; 657131, 3274706; 657121, 3274699; 657117, 3274708; 657109, 
3274717; 657100, 3274726; 657086, 3274733; 657073, 3274741; 657055, 
3274748; 657026, 3274758; 656999, 3274763; 656971, 3274771; 656947, 
3274771; 656924, 3274760; 656910, 3274741; 656890, 3274719; 656878, 
3274697; 656879, 3274675; 656882, 3274654; 656880, 3274637; 656885, 
3274627; 656897, 3274617; 656909, 3274590; 656920, 3274568; 656927, 
3274541; 656937, 3274511; 656943, 3274489; 656959, 3274465; 656955, 
3274438; 656967, 3274415; 656990, 3274402; 657010, 3274376; 657006, 
3274359; 656996, 3274337; 656993, 3274309; 656992, 3274289; 656994, 
3274257; 656999, 3274229; 657016, 3274209; 657039, 3274184; 657056, 
3274167; 657080, 3274163; 657099, 3274168; 657120, 3274181; 657145, 
3274186; 657166, 3274175; 657198, 3274160; 657210, 3274153; 657212, 
3274134; 657224, 3274126; 657237, 3274117; 657275, 3274101; 657296, 
3274099; 657318, 3274104; 657329, 3274118; 657338, 3274125; 657352, 
3274134; 657370, 3274140; 657382, 3274144; 657407, 3274141; 657437, 
3274138; 657475, 3274142; 657510, 3274144; 657533, 3274151; 657553, 
3274155; 657572, 3274174; 657583, 3274196; 657594, 3274218; 657616, 
3274234; 657636, 3274243; 657662, 3274249; 657681, 3274250; 657701, 
3274249; 657717, 3274237; 657735, 3274223; 657760, 3274193; 657784, 
3274159; 657805, 3274140; 657826, 3274102; 657843, 3274066; 657871, 
3274023; 657893, 3274005; 657930, 3273988; 657965, 3273982; 658005, 
3273986; 658068, 3273995; 658089, 3273997; 658116, 3274009; 658153, 
3274015; 658185, 3274021; 658213, 3274022; 658228, 3274013; 658241, 
3273993; 658237, 3273972; 658231, 3273928; 658219, 3273881; 658218, 
3273841; 658221, 3273783; 658222, 3273744; 658226, 3273664; 658225, 
3273618; 658207, 3273573; 658183, 3273548; 658172, 3273509; 658162, 
3273472; 658156, 3273429; 658159, 3273381; 658154, 3273347; 658133, 
3273311; 658094, 3273287; 658021, 3273264; 657921, 3273237; 657810, 
3273205; 657810, 3273206; 657760, 3273198; 657708, 3273189; 657663, 
3273182; 657651, 3273182; 657649, 3273245; 657645, 3273272; 657631, 
3273285; 657606, 3273290; 657578, 3273286; 657538, 3273282; 657514, 
3273287; 657504, 3273305; 657500, 3273328; 657501, 3273360; 657501, 
3273376; 657496, 3273388; 657488, 3273396; 657471, 3273400; 657456, 
3273402; 657431, 3273399; 657411, 3273392; 657397, 3273384; 657379, 
3273380; 657354, 3273367; 657338, 3273363; 657311, 3273372; 657280, 
3273401; 657251, 3273437; 657223, 3273482; 657201, 3273516; 657178, 
3273540; 657161, 3273553; 657140, 3273563; 657106, 3273580; 657072, 
3273588; 657043, 3273588; 657010, 3273581; 656994, 3273567; 656979, 
3273543; 656961, 3273511; 656939, 3273482; 656915, 3273451; 656882, 
3273429; 656842, 3273424; 656814, 3273424; 656793, 3273436; 656755, 
3273467; 656723, 3273491; 656701, 3273508; 656674, 3273527; 656645, 
3273539; 656620, 3273539; 656598, 3273535; 656571, 3273518; 656551, 
3273492; 656526, 3273475; 656497, 3273462; 656469, 3273454; 656437, 
3273445; 656408, 3273442; 656383, 3273445; 656362, 3273429; 656344, 
3273406; 656330, 3273381; 656328, 3273348; 656326, 3273320; 656324, 
3273289; 656322, 3273270; 656313, 3273237; 656308, 3273205; 656310, 
3273174; 656313, 3273133; 656317, 3273089; 656316, 3273040; 656317, 
3273012; 656304, 3273000; 656275, 3273000; 656247, 3273016; 656217, 
3273035; 656189, 3273055; 656158, 3273068; 656138, 3273076; 656123, 
3273073; 656111, 3273068; 656103, 3273047; 656103, 3273015; 656100, 
3272978; 656093, 3272939; 656087, 3272909; 656080, 3272871; 656059, 
3272824; 656038, 3272783; 656014, 3272749; 655982, 3272709; 655948, 
3272676; 655900, 3272642; 655854, 3272619; 655818, 3272598; 655769, 
3272576; 655730, 3272564; 655666, 3272570; 655623, 3272581; 655582, 
3272598; 655538, 3272625; 655511, 3272656; 655499, 3272689; 655490, 
3272712; 655481, 3272732; 655460, 3272744; 655433, 3272749; 655407, 
3272741; 655388, 3272721; 655376, 3272696; 655367, 3272675; 655359, 
3272652; 655354, 3272622; 655353, 3272585; 655349, 3272548; 655342, 
3272512; 655338, 3272486; 655298, 3272461; 655263, 3272461; 655231, 
3272475; 655201, 3272494; 655182, 3272506; 655169, 3272513; 655165, 
3272531; 655157, 3272549; 655153, 3272566; 655137, 3272590; 655122, 
3272611; 655107, 3272627; 655087, 3272642; 655066, 3272646; 655036,

[[Page 10405]]

3272640; 654995, 3272613; 654958, 3272588; 654925, 3272569; 654887, 
3272553; 654850, 3272533; 654814, 3272511; 654781, 3272475; 654752, 
3272439; 654737, 3272417; 654731, 3272386; 654734, 3272356; 654741, 
3272338; 654761, 3272303; 654796, 3272267; 654816, 3272241; 54839, 
3272214; 654858, 3272188; 654872, 3272152; 654917, 3272066; 654923, 
3272031; 654936, 3271984; 654948, 3271946; 654954, 3271914; 654965, 
3271876; 654960, 3271843; 654956, 3271819; 654933, 3271795; 654904, 
3271774; 654878, 3271751; 654858, 3271722; 654851, 3271695; 654861, 
3271665; 654861, 3271639; 654862, 3271607; 654857, 3271573; 654858, 
3271550; 654845, 3271532; 654818, 3271445; 654767, 3271281; 654744, 
3271216; 654693, 3271142; 654693, 3271116; 654693, 3271093; 654707, 
3271071; 654720, 3270997; 654731, 3270929; 654741, 3270886; 654749, 
3270839; 654761, 3270794; 654760, 3270749; 654768, 3270710; 654772, 
3270672; 654775, 3270626; 654780, 3270563; 654796, 3270529; 654806, 
3270495; 654818, 3270463; 654837, 3270427; 654857, 3270392; 654868, 
3270364; 654884, 3270327; 654911, 3270299; 654935, 3270265; 654942, 
3270253; 654925, 3270244; 654908, 3270229; 654894, 3270216; 654880, 
3270195; 654874, 3270176; 654857, 3270118; 654852, 3270080; 654855, 
3270043; 654867, 3269982; 654872, 3269941; 654880, 3269913; 654876, 
3269888; 654880, 3269864; 654881, 3269850; 654878, 3269847; 654885, 
3269818; 654896, 3269722; 654911, 3269660; 654977, 3269605; 55054, 
3269551; 655119, 3269467; 655155, 3269408; 655158, 3269331; 655137, 
3269264; 655123, 3269229; 655115, 3269175; 655106, 3269125; 655108, 
3269085; 655117, 3269026; 655129, 3268978; 655149, 3268932; 655173, 
3268870; 655208, 3268799; 655256, 3268758; 655296, 3268744; 655357, 
3268718; 655401, 3268688; 655430, 3268655; 655459, 3268614; 655483, 
3268567; 655519, 3268504; 655546, 3268460; 655569, 3268409; 655608, 
3268370; 655639, 3268346; 655662, 3268308; 655721, 3268293; 655776, 
3268290; 655814, 3268290; 655859, 3268298; 655913, 3268304; 655963, 
3268323; 656023, 3268342; 656063, 3268364; 656122, 3268379; 656184, 
3268393; 656234, 3268394; 656292, 3268394; 656341, 3268393; 656382, 
3268383; 656400, 3268360; 656408, 3268326; 656400, 3268296; 656375, 
3268260; 656341, 3268231; 656305, 3268201; 656271, 3268173; 656246, 
3268147; 656214, 3268111; 656188, 3268071; 656174, 3268017; 656174, 
3267966; 656177, 3267913; 656196, 3267861; 656219, 3267813; 656211, 
3267800; 656181, 3267795; 656118, 3267772; 656070, 3267755; 656033, 
3267732; 655989, 3267706; 655926, 3267669; 655859, 3267631; 655814, 
3267612; 655754, 3267578; 655594, 3267469; 655542, 3267441; 655428, 
3267405; 655402, 3267405; 655341, 3267409; 655289, 3267389; 655240, 
3267341; 655179, 3267285; 655149, 3267271; 655104, 3267233; 655060, 
3267200; 655029, 3267171; 654985, 3267115; 654946, 3267070; 654915, 
3267040; 654843, 3267015; 654803, 3267014; 654755, 3267022; 654717, 
3267030; 654675, 3267049; 654634, 3267070; 654606, 3267093; 654579, 
3267115; 654554, 3267153; 654531, 3267182; 654496, 3267193; 654482, 
3267211; 654463, 3267240; 654456, 3267256; 654470, 3267272; 654479, 
3267301; 654486, 3267330; 654476, 3267368; 654460, 3267411; 654444, 
3267449; 654426, 3267489; 654408, 3267538; 654402, 3267582; 654408, 
3267627; 654408, 3267666; 654397, 3267701; 654375, 3267740; 654356, 
3267768; 654340, 3267799; 654334, 3267820; 654330, 3267869; 654311, 
3267887; 654277, 3267918; 654230, 3267929; 654181, 3267930; 654155, 
3267909; 654117, 3267885; 654086, 3267863; 654029, 3267858; 653993, 
3267855; 653931, 3267852; 653898, 3267859; 653872, 3267878; 653864, 
3267909; 653868, 3267933; 653880, 3267959; 653884, 3267993; 653891, 
3268026; 653892, 3268062; 653894, 3268106; 653898, 3268138; 653917, 
3268182; 653925, 3268201; 653941, 3268234; 653965, 3268264; 653969, 
3268279; 653972, 3268308; 653985, 3268337; 653989, 3268356; 653991, 
3268393; 653991, 3268413; 653991, 3268437; 653995, 3268463; 653995, 
3268490; 653996, 3268536; 653999, 3268567; 653996, 3268606; 653989, 
3268643; 653981, 3268702; 653967, 3268757; 653952, 3268821; 653933, 
3268872; 653920, 3268929; 653896, 3268985; 653865, 3269038; 653821, 
3269095; 653775, 3269149; 653735, 3269196; 653671, 3269255; 653636, 
3269289; 653567, 3269345; 653522, 3269397; 653475, 3269469; 653446, 
3269524; 653400, 3269577; 653359, 3269610; 653307, 3269624; 653279, 
3269618; 653252, 3269608; 653216, 3269608; 653171, 3269601; 653137, 
3269595; 653110, 3269610; 653082, 3269627; 653063, 3269650; 653032, 
3269676; 652994, 3269698; 652947, 3269735; 652913, 3269779; 652875, 
3269820; 652839, 3269859; 652813, 3269891; 652783, 3269908; 652755, 
3269919; 652724, 3269934; 652690, 3269962; 652661, 3269985; 652643, 
3270010; 652643, 3270040; 652650, 3270092; 652658, 3270138; 652668, 
3270183; 652678, 3270234; 652684, 3270298; 652688, 3270331; 652705, 
3270365; 652712, 3270393; 652721, 3270456; 652730, 3270535; 652732, 
3270568; 652739, 3270606; 652745, 3270653; 652775, 3270703; 652773, 
3270754; 652764, 3270792; 652749, 3270840; 652708, 3270896; 652650, 
3270962; 652550, 3271052; 652430, 3271141; 652305, 3271253; 652108, 
3271473; 651976, 3271636; 651887, 3271755; 651828, 3271867; 651782, 
3271967; 651742, 3272066; 651712, 3272126; 651705, 3272185; 651706, 
3272241; 651676, 3272301; 651597, 3272362; 651581, 3272369; 651511, 
3272412; 651451, 3272459; 651423, 3272477; 651378, 3272498; 651314, 
3272514; 651266, 3272513; 651222, 3272510; 651189, 3272491; 651146, 
3272463; 651107, 3272430; 651077, 3272395; 651061, 3272354; 651039, 
3272300; 651032, 3272269; 651019, 3272223; 651006, 3272172; 651005, 
3272127; 651004, 3272081; 651004, 3272017; 651008, 3271935; 650996, 
3271865; 650973, 3271823; 650939, 3271807; 650899, 3271800; 650842, 
3271803; 650793, 3271815; 650755, 3271827; 650698, 3271849; 650634, 
3271875; 650549, 3271922; 650493, 3271954; 650447, 3271992; 650413, 
3272024; 650389, 3272056; 650373, 3272085; 650353, 3272126; 650353, 
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3272529; 650387, 3272595; 650374, 3272660; 650367, 3272709; 650357, 
3272756; 650346, 3272779; 650334, 3272820; 650316, 3272855; 650301, 
3272881; 650275, 3272910; 650258, 3272937; 650246, 3272954; 650224, 
3272969; 650190, 3272984; 650167, 3272990; 650135, 3272986; 650092, 
3272980; 650060, 3272969; 650036, 3272956; 650012, 3272931; 649985, 
3272902; 649970, 3272867; 649942, 3272833; 649934, 3272794; 649924, 
3272769; 649923, 3272738; 649914, 3272696; 649900, 3272652; 649893, 
3272617; 649881, 3272576; 649865, 3272528; 649854, 3272492; 649831, 
3272461; 649794, 3272426; 649761, 3272402; 649727, 3272392; 649678, 
3272395; 649647, 3272413; 649619, 3272450; 649613, 3272469; 649605, 
3272529; 649603, 3272562; 649608, 3272606; 649616, 3272653; 649629, 
3272692; 649644, 3272735; 649656, 3272771; 649674, 3272808; 649688, 
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[[Page 10406]]

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3273053; 649586, 3273057; 649541, 3273051; 649509, 3273037; 649477, 
3273023; 649436, 3273003; 649406, 3272988; 649380, 3272974; 649347, 
3272959; 649309, 3272942; 649264, 3272924; 649221, 3272911; 649191, 
3272902; 649149, 3272877; 649085, 3272840; 649040, 3272815; 649005, 
3272790; 648983, 3272771; 648958, 3272743; 648917, 3272701; 648884, 
3272661; 648857, 3272615; 648830, 3272558; 648808, 3272521; 648788, 
3272460; 648766, 3272396; 648725, 3272345; 648690, 3272310; 648637, 
3272287; 648585, 3272276; 648541, 3272276; 648495, 3272291; 648464, 
3272310; 648430, 3272335; 648405, 3272366; 648392, 3272395; 648383, 
3272433; 648390, 3272454; 648408, 3272488; 648438, 3272516; 648481, 
3272539; 648533, 3272565; 648567, 3272582; 648608, 3272602; 648647, 
3272623; 648688, 3272650; 648715, 3272673; 648737, 3272704; 648759, 
3272737; 648776, 3272774; 648783, 3272820; 648783, 3272854; 648779, 
3272886; 648772, 3272911; 648759, 3272943; 648746, 3272965; 648718, 
3272991; 648684, 3273013; 648646, 3273035; 648612, 3273043; 648556, 
3273056; 648508, 3273057; 648466, 3273055; 648428, 3273040; 648375, 
3273020; 648313, 3272987; 648271, 3272961; 648237, 3272947; 648198, 
3272944; 648149, 3272956; 648125, 3272984; 648091, 3273023; 648056, 
3273049; 648014, 3273076; 647974, 3273080; 647914, 3273072; 647847, 
3273053; 647768, 3273028; 647731, 3273017; 647706, 3273023; 647700, 
3273063; 647729, 3273159; 647751, 3273228; 647740, 3273276; 647702, 
3273341; 647651, 3273421; 647623, 3273483; 647629, 3273527; 647676, 
3273560; 647736, 3273589; 647827, 3273624; 647880, 3273648; 647919, 
3273666; 647931, 3273691; 647924, 3273726; 647897, 3273784; 647875, 
3273823; 647862, 3273846; 647818, 3273894; 647786, 3273934; 647745, 
3273972; 647720, 3274000; 647696, 3274038; 647685, 3274067; 647683, 
3274096; 647685, 3274131; 647702, 3274189; 647727, 3274240; 647740, 
3274262; 647756, 3274286; 647760, 3274308; 647745, 3274319; 647716, 
3274308; 647676, 3274282; 647638, 3274266; 647616, 3274266; 647598, 
3274271; 647575, 3274294; 647572, 3274315; 647575, 3274337; 647584, 
3274361; 647602, 3274399; 647619, 3274447; 647615, 3274480; 647596, 
3274500; 647558, 3274498; 647511, 3274498; 647471, 3274488; 647446, 
3274481; 647419, 3274479; 647391, 3274494; 647371, 3274500; 647355, 
3274520; 647327, 3274545; 647311, 3274565; 647288, 3274565; 647288, 
3274579; 647300, 3274598; 647281, 3274611; 647270, 3274601; 647223, 
3274561; 647200, 3274538; 647158, 3274514; 647118, 3274494; 647085, 
3274483; 647057, 3274471; 647027, 3274453; 647020, 3274435; 647017, 
3274405; 647033, 3274365; 647033, 3274339; 647048, 3274288; 647047, 
3274258; 647006, 3274210; 646963, 3274200; 646928, 3274186; 646892, 
3274189; 646875, 3274202; 646870, 3274217; 646870, 3274241; 646854, 
3274257; 646833, 3274270; 646804, 3274270; 646782, 3274277; 646773, 
3274298; 646770, 3274317; 646759, 3274344; 646746, 3274366; 646736, 
3274386; 646713, 3274409; 646699, 3274429; 646682, 3274456; 646675, 
3274483; 646642, 3274496; 646624, 3274505; 646594, 3274533; 646542, 
3274578; 646495, 3274618; 646467, 3274640; 646397, 3274696; 646350, 
3274749; 646332, 3274806; 646324, 3274835; 646327, 3274937; 646333, 
3274986; 646343, 3275021; 646369, 3275062; 646402, 3275095; 646431, 
3275131; 646440, 3275173; 646419, 3275212; 646373, 3275255; 646319, 
3275282; 646286, 3275294; 646262, 3275300; 646243, 3275333; 646241, 
3275375; 646227, 3275468; 646213, 3275539; 646185, 3275605; 646171, 
3275658; 646107, 3275731; 646032, 3275768; 645931, 3275801; 645847, 
3275808; 645784, 3275837; 645749, 3275856; 645748, 3275904; 645774, 
3275924; 645788, 3275956; 645802, 3276062; 645828, 3276271; 645840, 
3276413; 645847, 3276568; 645842, 3276653; 645870, 3276686; 645936, 
3276730; 645960, 3276769; 646017, 3276818; 646067, 3276847; 646065, 
3276932; 646071, 3277002; 646068, 3277061; 646068, 3277082; 646069, 
3277150; 646065, 3277194; 646064, 3277224; 646069, 3277254; 646072, 
3277317; 646067, 3277403; 646068, 3277465; 646076, 3277540; 646072, 
3277620; 646060, 3277663; 646063, 3277695; 646060, 3277732; 646058, 
3277774; 646055, 3277821; 646055, 3277854; 646017, 3277887; 645986, 
3277905; 645927, 3277925; 645878, 3277929; 645829, 3277933; 645751, 
3277952; 645710, 3277960; 645662, 3277989; 645621, 3278028; 645587, 
3278061; 645555, 3278085; 645510, 3278113; 645475, 3278136; 645427, 
3278171; 645388, 3278207; 645351, 3278239; 645314, 3278253; 645278, 
3278273; 645233, 3278281; 645206, 3278273; 645153, 3278259; 645110, 
3278256; 645049, 3278270; 645001, 3278293; 644956, 3278310; 644912, 
3278327; 644867, 3278347; 644823, 3278347; 644780, 3278346; 644725, 
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3278346; 644483, 3278346; 644459, 3278339; 644418, 3278339; 644350, 
3278333; 644299, 3278334; 644237, 3278337; 644157, 3278334; 644078, 
3278326; 644047, 3278329; 643928, 3278326; 643863, 3278325; 643713, 
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3278319; 643396, 3278304; 643346, 3278257; 643311, 3278224; 643277, 
3278191; 643268, 3278158; 643269, 3278117; 643271, 3278067; 643221, 
3278075; 643057, 3278178; 642339, 3278623; 642496, 3278776; 642565, 
3278860; 642476, 3278908; 642746, 3279121; 642804, 3279075; 642772, 
3279059; 642821, 3278971; 642987, 3278846; 643058, 3278925; 643091, 
3278938; 643040, 3279082; 643071, 3279112; 643158, 3278950; 643291, 
3278967; 643549, 3279000; 643578, 3279112; 643624, 3279108; 643673, 
3279000; 644168, 3279066; 644139, 3279170; 644235, 3279195; 644389, 
3279112; 644530, 3279004; 644634, 3278942; 644767, 3279079; 644804, 
3279241; 644842, 3279303; 644742, 3279416; 644796, 3279461; 644900, 
3279478; 644968, 3279638; 644966, 3279641; 645096, 3279725; 644983, 
3279834; 645089, 3279959; 644988, 3280037; 644805, 3280178; 644717, 
3280256; 644514, 3280425; 644169, 3280057; 643938, 3279907; 643892, 
3279964; 643915, 3280091; 644077, 3280218; 644158, 3280438; 644088, 
3280530; 643950, 3280426; 643857, 3280288; 643800, 3280218; 643684, 
3280276; 643592, 3280403; 643534, 3280541; 643557, 3280807; 643638, 
3280876; 643684, 3280992; 643604, 3281107; 643557, 3281234; 643500, 
3281315; 643511, 3281465; 643488, 3281603; 643592, 3281719; 643683, 
3281886; 643845, 3281875; 643937, 3281932; 644053, 3281990; 644099, 
3282048; 644110, 3282198; 644156, 3282279; 644214, 3282371; 644318, 
3282440; 644491, 3282475; 644618, 3282463; 644757, 3282544; 644918, 
3282636; 645022, 3282683; 645137, 3282798; 645230, 3282890; 645426, 
3282879; 645553, 3282902; 645645, 3283052; 645726, 3283202; 645668, 
3283294; 645611, 3283548; 645692, 3283675; 645761, 3283698; 645795, 
3283848; 645876, 3283906; 646003, 3283825; 646095, 3283733; 646142, 
3283594; 646292, 3283548; 646430, 3283560; 646580, 3283652; 646650, 
3283837; 646696, 3284033; 646692, 3284041; 646702, 3284059; 646696, 
3284104; 646678, 3284144; 646664, 3284182; 646661, 3284225; 646660, 
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[[Page 10407]]

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3284328; 646525, 3284312; 646514, 3284299; 646491, 3284290; 646457, 
3284278; 646432, 3284272; 646409, 3284250; 646377, 3284246; 646344, 
3284242; 646309, 3284241; 646272, 3284243; 646239, 3284245; 646207, 
3284257; 646199, 3284261; 646195, 3284269; 646182, 3284271; 646157, 
3284288; 646135, 3284307; 646119, 3284362; 646104, 3284376; 646100, 
3284399; 646092, 3284426; 646091, 3284436; 646092, 3284447; 646096, 
3284484; 646107, 3284517; 646120, 3284540; 646141, 3284569; 646162, 
3284603; 646190, 3284627; 646221, 3284652; 646246, 3284679; 646270, 
3284708; 646289, 3284726; 646305, 3284750; 646305, 3284775; 646311, 
3284794; 646303, 3284810; 646299, 3284833; 646303, 3284857; 646308, 
3284881; 646308, 3284906; 646305, 3284923; 646293, 3284947; 646283, 
3284966; 646275, 3284984; 646413, 3285176; 646352, 3285213; 646286, 
3285246; 646225, 3285283; 646153, 3285323; 646082, 3285356; 646022, 
3285385; 645994, 3285411; 645949, 3285427; 645910, 3285439; 645875, 
3285458; 645842, 3285476; 645787, 3285508; 645715, 3285534; 645660, 
3285561; 645604, 3285593; 645449, 3285663; 645214, 3285784; 644902, 
3285931; 644526, 3286110; 644194, 3286287; 644089, 3286311; 643589, 
3286585; 642774, 3286969; 642338, 3287196; 641946, 3287386; 641629, 
3287524; 641369, 3287651; 641162, 3287767; 641000, 3287899; 640810, 
3288147; 640556, 3288470; 640401, 3288660; 640141, 3288989; 639922, 
3289248; 639784, 3289375; 639519, 3289600; 639426, 3289687; 639230, 
3289906; 639138, 3290079; 639040, 3290229; 638902, 3290332; 638775, 
3290361; 638561, 3290396; 638498, 3290425; 638192, 3290794; 638192, 
3290846; 638164, 3290909; 638037, 3291001; 637887, 3291140; 637800, 
3291267; 637685, 3291353; 637529, 3291399; 637431, 3291468; 637253, 
3291549; 637137, 3291566; 637010, 3291566; 636907, 3291566; 636780, 
3291618; 636653, 3291659; 636543, 3291653; 636445, 3291751; 636301, 
3291832; 636151, 3291901; 635967, 3291993; 635788, 3292045; 635732, 
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3293055; 633166, 3293030; 631645, 3293030; 631632, 3293076; 631627, 
3293123; 631622, 3293164; 631621, 3293216; 631615, 3293257; 631580, 
3293287; 631552, 3293317; 631524, 3293340; 631494, 3293385; 631474, 
3293424; 631453, 3293453; 631423, 3293477; 631394, 3293499; 631364, 
3293524; 631356, 3293551; 631344, 3293598; 631333, 3293620; 631318, 
3293633; 631294, 3293639; 631259, 3293637; 631230, 3293641; 631218, 
3293662; 631216, 3293698; 631222, 3293737; 631214, 3293778; 631202, 
3293797; 631173, 3293809; 631150, 3293819; 631126, 3293839; 631097, 
3293835; 631072, 3293822; 631044, 3293825; 631000, 3293859; 630955, 
3293889; 630923, 3293911; 630886, 3293945; 630850, 3293970; 630856, 
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3294051; 630797, 3294067; 630796, 3294086; 630799, 3294108; 630802, 
3294130; 630797, 3294146; 630788, 3294152; 630764, 3294163; 630744, 
3294168; 630733, 3294182; 630726, 3294215; 630723, 3294226; 630717, 
3294234; 630704, 3294231; 630689, 3294226; 630678, 3294233; 630673, 
3294258; 630665, 3294281; 630660, 3294302; 630654, 3294319; 630678, 
3294330; 630703, 3294337; 630723, 3294343; 630739, 3294357; 630738, 
3294382; 630736, 3294425; 630742, 3294469; 630752, 3294499; 630760, 
3294535; 630767, 3294571; 630778, 3294601; 630794, 3294631; 630807, 
3294657; 630835, 3294693; 630865, 3294731; 630883, 3294751; 630889, 
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3294915; 630897, 3294951; 630897, 3294969; 630890, 3294991; 630889, 
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3295099; 630889, 3295128; 630887, 3295156; 630897, 3295174; 630919, 
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3295284; 630942, 3295303; 630940, 3295312; 630455, 3295226; 630079, 
3295163; 629878, 3295136; 629724, 3295119; 629662, 3295114; 629659, 
3295174; 629662, 3295343; 629652, 3295351; 629543, 3295363; 29391, 
3295380; 629251, 3295390; 629136, 3295405; 629091, 3295409; 629020, 
3295414; 629026, 3295470; 629026, 3295492; 629028, 3295541; 629028, 
3295588; 628915, 3295594; 628904, 3295590; 628879, 3295582; 628340, 
3295566; 628289, 3295566; 628264, 3295573; 628236, 3295584; 628213, 
3295596; 628142, 3295646; 628076, 3295680; 628019, 3295700; 627975, 
3295713; 627926, 3295711; 627877, 3295700; 627832, 3295675; 627778, 
3295635; 627736, 3295597; 627683, 3295564; 627645, 3295549; 627577, 
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3295881; 626224, 3295904; 626174, 3295924; 626118, 3295950; 626052, 
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3296100; 625783, 3296123; 625711, 3296137; 625658, 3296137; 625588, 
3296131; 625523, 3296110; 625451, 3296093; 625392, 3296087; 625302, 
3296080; 625260, 3296080; 625235, 3296506; 625093, 3296558; 625087, 
3296694; 625043, 3296698; 625013, 3296631; 624862, 3296699; 624704, 
3296782; 624379, 3296873; 624266, 3297016; 624107, 3297077; 623850, 
3297099; 623654, 3297069; 623677, 3296752; 622786, 3296805; 622778, 
3296631; 622536, 3296624; 622521, 3296525; 622106, 3296314; 622008, 
3296450; 621577, 3296284; 621577, 3296065; 620996, 3295823; 621033, 
3295732; 620474, 3295554; 620303, 3295919; 619268, 3295574; 619136, 
3295673; 619071, 3296018; 618709, 3295968; 618151, 3296165; 618200, 
3295738; 617740, 3295229; 617855, 3294999; 617757, 3294786; 617330, 
3294638; 617139, 3294362; 615591, 3295247; 615704, 3295492; 615950, 
3295919; 615490, 3296215; 615507, 3296461; 615392, 3296773; 614518, 
3296828; 614204, 3297382; 613907, 3298112; 613610, 3298773; 613525, 
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3299383; 614090, 3299455; 614121, 3299594; 614140, 3299701; 614440, 
3299862; 614499, 3299872; 614575, 3299877; 614604, 3299886; 614743, 
3300083; 614784, 3300155; 614819, 3300212; 614808, 3300335; 614817, 
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3300627; 615177, 3300691; 615191, 3300729; 615234, 3300770; 615347, 
3300797; 615454, 3300795; 615593, 3300740; 615703, 3300682; 615804, 
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3300293; 615969, 3300230; 615969, 3300184; 615988, 3300145; 616026, 
3300129; 616119, 3300115; 616185, 3300113; 616237, 3300126; 616295, 
3300132; 616347, 3300096; 616396, 3300044; 616437, 3299989; 616453, 
3299967; 616522, 3300184; 616612, 3300414; 616832, 3300967; 616884, 
3301093; 616911, 3301178; 616914, 3301216; 616993, 3301959; 617021, 
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[[Page 10408]]

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3305950; 605192, 3306026; 605184, 3306093; 605107, 3306098; 605011, 
3306084; 604876, 3306077; 604779, 3306064; 604680, 3306057; 604610, 
3306077; 604532, 3306127; 604433, 3306215; 604172, 3306487; 604053, 
3306649; 603936, 3306813; 603853, 3306930; 603756, 3307074; 603733, 
3307116; 603715, 3307173; 603704, 3307249; 603693, 3307427; 603702, 
3307568; 603722, 3307613; 603767, 3307663; 603790, 3307735; 603821, 
3307886; 603830, 3307982; 603830, 3308097; 603830, 3308209; 603855, 
3308279; 603902, 3308333; 603933, 3308362; 603963, 3308421; 604003, 
3308486; 604071, 3308612; 604156, 3308785; 604203, 3308907; 604230, 
3308943; 604316, 3309010; 604365, 3309068; 604428, 3309134; 604541, 
3309224; 604606, 3309282; 604682, 3309363; 604770, 3309491; 604835, 
3309563; 604948, 3309651; 605094, 3309725; 605224, 3309763; 605368, 
3309833; 605488, 3309885; 605589, 3309916; 605685, 3309930; 605728, 
3309919; 605755, 3309892; 605782, 3309862; 605816, 3309860; 605852, 
3309878; 605886, 3309914; 605926, 3309932; 605967, 3309941; 605993, 
3309947; 606019, 3309962; 606041, 3309983; 606057, 3309989; 606078, 
3309987; 606102, 3309979; 606119, 3309985; 606134, 3310008; 606143, 
3310049; 606151, 3310074; 606168, 3310089; 606188, 3310099; 606213, 
3310103; 606245, 3310110; 606270, 3310126; 606281, 3310149; 606295, 
3310165; 606315, 3310177; 606343, 3310185; 606365, 3310202; 606384, 
3310235; 606405, 3310275; 606421, 3310305; 606429, 3310337; 606446, 
3310356; 606483, 3310382; 606509, 3310402; 606533, 3310426; 606544, 
3310451; 606558, 3310488; 606577, 3310520; 606591, 3310540; 606610, 
3310556; 606630, 3310561; 606656, 3310563; 606681, 3310573; 606710, 
3310593; 606729, 3310624; 606733, 3310664; 606740, 3310701; 606740, 
3310722; 606753, 3310750; 606766, 3310771; 606774, 3310795; 606779, 
3310829; 606787, 3310855; 606802, 3310876; 606831, 3310898; 606839, 
3310919; 606852, 3310937; 606872, 3310946; 606892, 3310947; 606913, 
3310943; 606938, 3310939; 606953, 3310926; 606964, 3310926; 606986, 
3310931; 607004, 3310942; 607019, 3310954; 607029, 3310975; 607040, 
3310996; 607056, 3311008; 607073, 3311020; 607099, 3311026; 607122, 
3311050; 607131, 3311078; 607126, 3311161; 607131, 3311175; 607538, 
3311098; 608006, 3311007; 608453, 3310919; 608470, 3310925; 608557, 
3311197; 608583, 3311278; 608592, 3311312; 608611, 3311339; 608631, 
3311364; 608898, 3311185; 608929, 3311172; 608958, 3311169; 609115, 
3311172; 609332, 3311177; 609407, 3311181; 609403, 3311336; 609416, 
3311360; 609438, 3311374; 609472, 3311377; 609504, 3311379; 609537, 
3311389; 609571, 3311390; 609589, 3311398; 609605, 3311406; 609605, 
3311368; 609604, 3311321; 609614, 3311305; 609637, 3311297; 609656, 
3311309; 609652, 3311330; 609657, 3311349; 609672, 3311352; 609720, 
3311346; 609724, 3311362; 609732, 3311378; 609732, 3311395; 609741, 
3311412; 609762, 3311410; 665152, 3281996; 665162, 3281729; 665585, 
3281731; 665579, 3282052; 665281, 3282042; 665275, 3282002; 665152, 
3281996.
    (ii) Note: Map of Unit 3, Lower Atchafalaya River Basin (Map 4), 
follows:
BILLING CODE 4310-55-P

[[Page 10409]]

[GRAPHIC] [TIFF OMITTED] TR10MR09.003

* * * * *

    Dated: February 20, 2009.
Jane Lyder,
Assistant Deputy Secretary, Department of the Interior.
[FR Doc. E9-4536 Filed 3-9-09; 8:45 am]
BILLING CODE 4310-55-C