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detected when more than 225 individuals were collected (Figure 3). Similarly, Matthews (1990) found that spatial variance was greater than tem- poral variance and suggested that in sh surveys it is better to increase the number of sampling sites than the number of visits per site. Water samples were collected in a 4-L cubitainer and in two 60-mL syringes lled from a owing area at the downstream end of each reach (Peck. Our objective was to determine an appropriate raft electroshing effort for rivers 10150 m wide with widely varying velocities and habitats rang- ing from pools many meters deep to rifes a few centimeters deep. Lars en, and. Over 80 of the CW p 95 variance was not accounted for by these associations, mean- ing that habitat would not be useful for predeter- mining sampling effort. The fish samples were classified with a Kohonen artificial neural network and assigned to two main clusters (X and Y) and, respectively, two pairs of subclusters (X1, X2; Y1, Y2) of neurons.


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Greg- ory, a. Natural regeneration of fish assemblages in the Pilica River after reduction of point source pollution Tadeusz Penczak Andrzej Kruk Tadeusz Penczak Electrofishing was conducted along the Pilica River, the biggest West tributary of the Vistula, Poland. In other words, there was four times as much within-reach variance (measured as the temporal and measurement variance among subreaches at a reach) as there was among-reach variance in the distance needed to collect 95 of the species. This research was funded by the usepa through contract 68-D01005 with Dy- 1239 elect ROF ISH instan CE TT IMA TE SP ECI ECH NES S namac, Cooperative Agreement 824682 with Oregon State University, and contract 68-W01 032 with CSC Corporation. Keating and Quinn (1998) dem- onstrated that the Michaelis-Menten model per- formed poorly when there were many species over- all and many rare species. All content in this area was uploaded by John.

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For small sample sizes in all studied communities (less than 25 of the total community the least biased estimator was the second-order jackknife, followed by the first-order jackknife, the bootstrap, and the simple richness estimator. Johns (NET: 40, SOS: 47) : I wasnt going to write about the Johnnies here because they entered the day as. We sampled very few rivers with highly braided channels or complex off-channel habitats (alcoves, ponds such sys- tems could also require alternative sampling meth- ods. The collected numbers of species wer e typically only 03 s pecies fewer than those predicted for true species richness by simul ated species accumulation cur ves and nonparametric models. Some researchers employ multiple gears to assess different habitats and capture additional species, but electroshing is less selective and more widely applicable than the other techniques for monitoring sh assemblages (Hendricks. North Am erican Journal of Fisheries Management 12:198 203.