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<br />14 <br /> <br />I <br />I <br />I <br />I <br />1 <br />I <br />I <br />I <br />I <br />j <br />I <br />I <br />I <br />\ <br />I <br />l <br />I <br />l <br />E <br /> <br />still occurring in the San Juan River and, because of this certainty, our larval fish sampling efforts for this <br />minnow could be different than those for razorback sucker. <br /> <br />As numerous Upper Colorado River basin researchers had reported light-traps as one of the best means of <br />co lIecting larval razorback sucker, we too elected to use that sampling procedure during the first year (calendar <br />year 1997) of sampling. The only previous San Juan River fish investigation that employed light-traps was in <br />1994-1995 (conducted by the National Park Service) near the San Juan River-Lake Powell confluence. The <br />1994 sampling effort produced an extremely large number of larval fish (ca. 25,000) from a modest number of <br />samples (n=20), of which over 99% were red shiner. Similar sampling in 1995 yielded 25,455 specimens in 47 <br />light-traps samples and as in 1994, red shiner numerically dominated the catch. No Colorado pikeminnow or <br />razorback sucker were taken in the 1994-1995 light-trap sampling efforts. <br /> <br />During the 1997 razorback sucker larval fish survey, light traps were set nightly in low-velocity habitats <br />between Aneth and Mexican Hat from late March through mid-June 1997. The traps were distributed at dusk <br />and retrieved about four hours later. Fish taken in those samples were preserved in the field, Sampling success <br />during the 1997 razorback sucker larval fish study was quite poor. While there were over 200 light-trap sets, <br />those sampling efforts produced only 297 fish. Of those, about 200 (66%) were larval suckers (either <br />flannelmouth sucker or bluehead sucker). Larval razorback sucker were not present in the 1997 sampling <br />survey. While there were probably several factors to account for the poor light trap catch rate, a principal factor <br />was the limited access to suitable habitats. Light traps are most effective when set in habitats with little or no <br />water velocity. During our driving survey of riverine habitats in the region (March 1997), we identified <br />numerous locations that appeared to be suitable sites for light trap sampling. However, we found that high flow <br />in the San Juan River eliminated virtually all previously identified low velocity habitats. Further driving <br />reconnaissance failed to yield additional locations to set light traps. Being tied to specific collecting sites was <br />not the most efficient means of collecting large numbers of individuals. <br /> <br />In 1998 we modified our sampling technique to allow for the sampling of a greater portion of the San Juan <br />River and the collection of a significantly larger number of larval fish over a wider reach of the river. We <br />conducted sampling forays (n=6) at approximately bi-weekly intervals from 17 April (first trip - no larval <br />suckers) to 6 June 1998 between the Four Corners drift-net station (RM 128) and Bluff (RM 80) and used both <br />active and passive sampling techniques to collect larval fish. The primary sampling method was a fine mesh <br />larval seine (in 1998, we collected more larval sucker in a single seine sample than in all of the 1997 light trap <br />samples). Passive sampling techniques were both drift-netting and the use of light-traps, Drift-nets were set <br />periodically to determine if larvaJ sucker comprised a significant portion of the drift community while light- <br />traps were set adjacent to campsites if appropriate aquatic mesohabitats could be located. An inflatable raft was <br />used to traverse this river reach and allow investigators the opportunity to sample habitats that were either not <br />formerly accessible or observable under the constraints of the previous sampling protocol. <br /> <br />The 1998 sampling protocol resulted in the collection of over \3,000 specimens, the majority of which were <br />larval catostomids. This 43-fold increase in number of specimens, as compared with 1997, provided <br />substantially better resolution of spawning periodicity of the sucker community. In addition, the 1998 samples <br />produced enough individuals for investigators to determine, with a high degree of confidence, if razorback <br />sucker reproduction occurred in the San Juan River during that period, None of the aforementioned information <br />