Laserfiche WebLink
<br />13394 <br /> <br />Federal Register I VoL 59, No. 54 I Monda,x., March 21, 1994 I Rules and Regulations <br /> <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 <br /> <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, <br /> <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 <br />