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WSP09867
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Last modified
1/26/2010 2:56:19 PM
Creation date
10/12/2006 3:59:05 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8220.101.10.E
Description
Glen Canyon Dam/Lake Powell
State
AZ
Basin
Colorado Mainstem
Date
7/1/1998
Author
Arizona Game and Fis
Title
Biological Evaluation: Establishment of New Populations of Kanab Ambersnail in Grand Canyon (Coconino County - Arizona)
Water Supply Pro - Doc Type
Report/Study
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<br />Arizona Game and Fish Department <br />Biological Evaluation: Kanab Ambersnail <br /> <br />July 1998 <br />Page 10 <br /> <br />maintain refrigeration. Air temperature can be regulated by adding <br />or removing these insulating materials as required. A fine-mist <br />spray bottle with VP water will be used to maintain moisture and <br />humidity conditions. We recommend the transport of immature KASs <br />not exceed seven days in duration, while under environmentally <br />maintained conditions. During the 1996 BHBF, relocated KASs were <br />held in refrigerated containers for this duration without any <br />mortality (Stevens et al. 1997b). <br /> <br />Upon arrival to establishment sites, translocated KASs will be <br />released within specific areas to facilitate future mating success <br />and monitoring activities. Specific release areas are isolated <br />patches of primary vegetation that are outside normal recreation <br />use and are protected from possible natural disturbance. KASs will <br />be placed within a 1 to 4-m2 area of primary habitat at <br />establishment sites. Using entomological-grade forceps and/or <br />camel-hair brushes, KASs will be gently removed from the transport <br />containers and carefully placed on host vegetation at the new site. <br /> <br />The KASs collected for the TPZ refugium will remain in transport <br />containers (within ice chests) until delivery to TPZ. Upon arrival <br />at TPZ, KASs will be transferred from transport containers to one <br />of two habitat enclosures which have been developed at TPZ. AGFD <br />will monitor the KAS refugium population; information gathered will <br />include quantity of KASs, KAS behavior, presence of egg masses <br />(clutch size and appearance), presence of other invertebrates, and <br />condition of host vegetation. In addition, water quality (i.e., pH <br />and conductivity), discharge, air temperature and relative humidity <br />will also be measured within habitat enclosures and recorded in a <br />field logbook. This information will be used to assist in the <br />maintenance of the refugium habitat and provide data on refugium <br />population dynamics for interim and final reports to CUPCA, USBR, <br />USFWS, TPZ, and the KAWG in 1999. <br /> <br />Supplemental stocking of KASs at establishment sites and at TPZ <br />will occur in 1999 as needed to augment population density and <br />preserve genetic variability. AGFD recommends annually stocking a <br />minimum of 10 KASs (at least half will contribute reproductively) <br />up to maximum of 150 individuals if overwintering mortality is <br />higher than expected. Monitoring trips in September-October 1998 <br />and March-April 1999 will begin to evaluate initial establishment <br />success and need for further population augmentation. <br />
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