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<br />13394
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<br />Federal Register I VoL 59, No. 54 I Monda,x., March 21, 1994 I Rules and Regulations
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<br />role of the Colorado River native fish areas, these flows must be evaluated and
<br />eradication programs on listed fish in perhaps adjusted in the futme.
<br />the San Juan and Green Rivers. Including specific flows as constituent
<br />. Service Respcmse:1'he Draft elements would ~the rolemaking
<br />BiolQ8ical Support Document contains a process be followed to make changes in
<br />section that describes State and Federal recommended flows as research became
<br />fish removal projects on the San Juan available. This would create
<br />and Green Rivers 'These projects were administrative delays to respond to
<br />an allemptto temporarily remove native fishery research recommendations. The
<br />and nonnative. fishes from new reservoir flows used in Brookshire et aI. (1993)
<br />storage pools prior to sportfish stocking, were developed solely for use in the
<br />These projects were not expected to economic analysis. In reviewing the
<br />pennanently eradicate those species nor impacts of futUl'll Federal actiuns on
<br />were they intended to remove those critical habitat, the Service will use the
<br />species from entire river systems. These best scientific and commercial
<br />projects probably had little net effect on information available at that time, as
<br />listed species. . re'luired by the Act.
<br />--ISSUe-42:-Two.respondents,indicated__ ssue-45:.Se.vera1-respondents-were----
<br />that the Ur-oer Basin Recoverv concemed that the Service intended to
<br />Implementation ProgrlllIl was' not a poison all the ri~ to remove
<br />substitute for designation of critical nonnative fish and .that the poison
<br />habitat, would harm people, animals, plants,
<br />Service Response: The RIP is not a and the soil. They also indicated their
<br />substitute forth.. designation of critical displeasure con~eming th.loss of
<br />habitat: however, the Ultimate goal of sportfish to recover.the endal!8erad fish.
<br />both the RIP..amtthe designation is the Service RegpoIlSe: As stated
<br />recovery (dellstingl of these endangered previously, the designation of critical
<br />fish. It is the :intent-of the Service to habitat .does n~ require any particular
<br />analyze and 1IIII8I1d the section 7 management action or actions to occur.
<br />Agreement and Recovery Critical habitat serves to identify and
<br />ImplementationP>~dUl Recovery inventory those areas where ..'
<br />Action Plan of the RIP, as needed, in conserVation activities should occur. In
<br />order for it toi>e:'a reasonable and '. the development of any specific plan to
<br />prudent alternative for the destruction implement conservation actions in a
<br />or adverse modification of critical. particular critical habitat reach. the
<br />habitat for aU activities addressed by the sgency involved is required to follow all
<br />RIP;., :... "";' ,".'" Federal and State laws and regulations
<br />Issue 43: SoaN lllspOndents indicated prior to iml?lementing the action.
<br />that the additioiml..1ection criteria for The SerVice has identified the
<br />razorback sw:ksrWere too brOad, introduction of nonnative fish species
<br />. Service Respol188' Tne additional into the Basin as a significant cause of
<br />criteria used .toaid the Service in the decline of native fish species. It is
<br />selecting areas forproposa1 as critical likely that the implementation of
<br />habitat for theDZOrback sucker were conservation sctions may result in
<br />broad to account for the various habitat proposals to reduce the numbers of
<br />conditions, geographic areas, and life nonnative fish in a particular area.
<br />history reqnn.lItllmts throughout the Techniques to reduce nonnativa fish
<br />species' range. The species has been numbers include netting, trapping,
<br />shown to use a variaty of habitats electrofishing, liberalization of creel
<br />depending on geographic location and limits'and equiprilent restrictions,
<br />other factors SIlCh as nonnative fish physical habitat alterations or
<br />interactions thet affect their habitat. restoration, as well as the use of
<br />Given the wide variety of habitats used toxicants.
<br />by various lim stages ofrszorback The Service, or any other agency, is
<br />sucker, the Service does not believe the . requlred to follow Federal and State
<br />additional selection criteria were too laws and regulations in order to use fish
<br />broad" toxicants. These laws and regulations
<br />Issue 44: One respondent indicated are in place to protect nontarget
<br />that the final rule should include organisms (including people, animals,
<br />specified flows as constituent elements. plants, and soils) from adverse effects of
<br />Service Response: Tha Service does the toxicant. Fish toxicants in use toclay
<br />not believe it would be appropriate to have been used safely in rivers, ponds,
<br />have specific flows included as and reservoirs for many years.
<br />constituent elements because: (1) Flow Issue 46: A few respondents stated
<br />recommendations based upon site- or that unoccupied areas should not be
<br />river-specific research are unavailable designated as critical habitat, but
<br />for most criticalllabitat areas, and (2) designated experimental nonessential.
<br />even.thoughflow recommendations Service Response: The Service did not
<br />could be made for some critical habitat include erly unoccupied habitat in this
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<br />designation of CIitical habitat. All areas
<br />designated have recently'docwnanted
<br />occurrences of these fish and/or are
<br />traated as occupied habitat in section 7
<br />consultations. There are two
<br />experimental nonessential populations
<br />for the Colorado squawfish in tha Salt
<br />and Verde Rivers in 'Arizona. Ins hoped
<br />that the species can be reestablished in
<br />Arizona through work under this
<br />designation, Protection of the fishes and
<br />their habitat is greater under section 7
<br />of the Act compared with those
<br />provideil by the experimeIital
<br />nonessential population classification,
<br />which is intended to provide
<br />management flexlbility.
<br />Issue 47: Several respondents
<br />questioned why the San Juan River
<br />critical habitat for the razorback sucker
<br />ended at the Hoghack Diversion and
<br />extended to Fannington, New Mexico,
<br />for the Colorado squawfish.
<br />Service Response: Biological
<br />information on the razorback sucker
<br />indicates that this species has an affinity
<br />for low velocity habitats such as.
<br />backwaters and secondary channels.
<br />The geomorphology of the San Juan
<br />River below the Hogback Diversion
<br />provides these types ofhabffirts.. . .
<br />Upstream of the Hogback Diversion, the
<br />river channel is more restricted With
<br />faster.flowing, deeper water habitaiS,
<br />and few bacKwaters or seco:ildary
<br />channels are found. Thus, for the
<br />razorback sucker, the area upstiearn
<br />from the diversion dId not suIliciently .
<br />possess the primary constituent
<br />elements to justify its inclwiion as being
<br />necessary for this species' conservation.
<br />Biological information on the .-
<br />Colorado squawfish indicates that the
<br />adult fish use low velocity areas, but not
<br />as much as younger liIe stages. Adult
<br />Colorado squawfish often use more
<br />high-velocity or deep water river
<br />sections, si1nilax to those available in
<br />the reach of the San Juan River above
<br />the Hogback Diversion upstream to
<br />Farmington, New Mexico. This reach
<br />has been identified in. the Colorado
<br />Squawfish Recovary Plan as being
<br />needed for downlisting of this species,
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<br />Economic Issues
<br />
<br />Issue 48: Many respondents raised
<br />questions regarding the level of
<br />geograpbic disaggregation in the
<br />economic analysis.
<br />Service Response: The direct impacts
<br />of critical hsbitat designation were
<br />determined at the river reach level.
<br />Economic dsta were available at the
<br />county level in the IMPLAN data sets
<br />and formed the basis of the analysis.
<br />However, it is inappropIiat~ to conduct
<br />the economic analysis at the county
<br />level or tribal lands level because the
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