Laserfiche WebLink
Electrofishing a large river can be affected by a variety of factors such as <br />experience of the collectors, streamflow, turbidity, water temperature, etc. <br />Therefore, in order for data to be truly comparable, every effort should be made <br />to reduce and/or account for the many factors that could affect electrofishing <br />efficiency. Because of the large number of investigators and sampling designs <br />used to collect the data discussed here, many of these factors can not be <br />accounted for. Thus direct comparisons among years in an attempt to detect <br />changes in the adult population will not be meaningful. However, general <br />comparisons among years and or reaches may be useful to compare the relative <br />importance of the reaches or to examine changes in the size structure of the <br />population. <br />Post-Larval Colorado Squawfish Monitoring <br />A total of 17 files contained data that met the criteria for post-larval Colorado <br />squawfish monitoring (Table 3). Sampling programs very similar to the current <br />post-larval Colorado squawfish monitoring program were initiated by the Fish and <br />Wildlife Service in the Green River in 1979 and in the Colorado River in 1982. <br />The 1979 effort was relatively unstructured, with investigators simply proceeding <br />downstream and sampling backwaters as they came to them. However, in 1980 the <br />design included sampling one backwater with two seine hauls in each 5-mi reach <br />of river. This design forms the basis of the monitoring program. The early <br />sampling included the entire length of the river, so each of the designated <br />reaches was sampled completely in the earlier collections. Because the sampling <br />design was basically similar and the designated reaches were completely sampled <br />in the earlier collections, the earlier data should be reasonably comparable with <br />11