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PROCEEDINGS OF THE DESERT FISHES COUNCIL, 1994 SYMPOSIUM <br />concentrated in the Overton Arm and Gregg's <br />Basin/Grand Wash portions of the lake. An additional <br />eight records are from the Temple Bar area <br />immediately adjacent to the lower Gregg's Basin. <br />These areas, along with Las Vegas Wash, represent <br />inflow areas and tend to be more productive than the <br />relatively sterile central Virgin and Boulder basins. <br />Sampling efforts represent a broad base of sites, times <br />and methods throughout most areas of the reservoir. <br />Thirty of 44 documented NDOW contacts occurred in <br />the November to May period when razorbacks are <br />most likely to be found in shallow water littoral zones. <br />All of the NDOW records outside of that winter/spring <br />time frame occurred near or above Temple Bar. <br />No records of collections or contact with <br />razorback sucker could be found in available agency <br />field records between 1980 and 1990. Extensive gill <br />and trammel netting was conducted on Overton Arm <br />during the 1986-1988 period by the University of <br />Nevada, Las Vegas, in conjunction with the <br />cooperative nutrient enhancement project, including <br />sites where historic collections of adult razorbacks had <br />occurred. No records of razorback sucker captures <br />were found in field data files from those efforts. The <br />lack of observations or contacts incidental to other <br />routine sport fish sampling activities indicates a <br />probable reduction in occurrence when compared to <br />the more frequent observations through the early <br />1970's. However, changes in agency sampling <br />techniques in the 1980's, such as use of mid-water and <br />meter-net trawling and decreased use of conventional <br />net surveys, may have significantly decreased the <br />opportunity to contact or observe adult razorback <br />suckers for much of this period. <br />Current dedicated Lake Mead razorback survey <br />efforts began in April 1990 when NDOW personnel <br />observed an apparent spawning aggregation of <br />approximately 15 adult suckers in the Blackbird Point <br />area of Las Vegas Wash. Three adult razorbacks were <br />collected using electrofishing equipment and apparent <br />spawning behavior was observed. Specific sampling <br />efforts were not conducted in 1991, although a single <br />adult razorback sucker was captured at Bark Bay on <br />Overton Arm in March during spring gill net surveys. <br />Intensive trammel net surveys targeted <br />specifically at razorback suckers in known areas of <br />occurrence were initiated in spring 1992. Efforts were <br />concentrated at Blackbird Point, near Las Vegas Wash, <br />and Echo Bay on Overton Arm, based on 1990 <br />collections and reports of recent observations. A total <br />of 25 adult razorback suckers were captured at the two <br />locations, 12 at Blackbird Point and 13 at Echo Bay. <br />Efforts for 1993 were expanded to include <br />historic collection locations and other sites thought to <br />have characteristics of preferred razorback spawning <br />habitat, primarily the presence of well-washed coarse <br />gravel or cobble substrate and exposure to limited <br />wave action to reduce siltation. A total of 92 trammel <br />VOLUME XXVI - published 1995 <br />net nights of survey were conducted at 21 sites in all <br />four primary basins. The majority of sets were placed <br />in the January through April period. A total of 21 adult <br />razorback suckers were captured during 1993, all at <br />the Blackbird Point (11) and Echo Bay (10) sites. All <br />captures occurred in trammel net sets during the <br />months of February and April. In 1994 a total of 113 <br />trammel net nights of sampling effort were conducted <br />at 40 sites lakewide. A total of five razorback suckers <br />were captured, all at the Blackbird Point site. <br />Adult razorback suckers captured in Lake Mead <br />since 1990, with only two exceptions, have been <br />marked to facilitate identification in the event of <br />recapture. Initially five fish were tagged using Floy <br />brand T-lock anchor tags. Beginning in March 1992 all <br />adult fish were tagged using PIT tags provided by the <br />Bureau of Reclamation. Through 1994 a total of 42 <br />adult fish were marked by NDOW personnel using PIT <br />tags. A total of six recaptures of PIT tagged fish were <br />documented in 1993, from fish tagged in 1992 or <br />1993, three at Blackbird Point and three at the Echo <br />Bay site. <br />Observations of the historic population of <br />razorback suckers in Lake Mead appear to closely <br />follow predicted trends for captive populations in <br />lower basin mainstem reservoirs. Jonez and Sumner <br />(1954) reported razorbacks as abundant and <br />widespread throughout the lake with particular <br />seasonal occurrence in inflow and potential spawning <br />areas. In the early 1950's the impoundment was 15 to <br />20 years old and a logical assumption is that <br />entrapment of resident adult fish from dam closure or <br />a high level of survival and recruitment of juvenile fish <br />from spawning at the time of impoundment would <br />result in retention and observation of relatively large <br />numbers of older-aged adult fish at the time of their <br />studies. Jonez and Sumner specifically mentioned <br />observations of fish in the 290 mm to 620 mm or <br />larger size range, and that at no time were fish smaller <br />than 290 mm observed in Lake Mead. Although their <br />length estimates appear to be based only on visual <br />observations, and age estimation of adult razorbacks <br />based on length measurements is highly subjective, it <br />is probable that most of the adult fish observed by <br />Jonez and Sumner dated to a period at or near the time <br />of reservoir filling. Their lack of observations of <br />smaller adult fish supports the presumption that <br />significant recruitment to the population was not <br />occurring during this period. Both anecdotal and <br />documented observations throughout the historic <br />period indicate that adult fish were broadly distributed <br />throughout the reservoir, including upper lake areas to <br />Paiute Point and throughout the Overton Arm. A <br />decline in anecdotal observations of adult fish after the <br />mid-1960's correlates with the predicted longevity of <br />the species and indicates a probable loss of the original <br />cohort of adult fish to old age in the 1979s and 1980's. <br />25