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21 <br />t <br />1 I iV <br />I <br />J. - i - <br />ALASKA f <br />n„ <br />o <br />HAWAII <br />Fig. 1. National Pesticide Monitoring Program (NPMP) stations (numbered circles) where freshwater fish were collected for organochlorine <br />residue analyses. (Unnumbered circles represent stations not sampled during 1976-79.) <br />those reported in the past: common carp represented 22% <br />of the samples and were collected at 35% of the stations; <br />channel catfish, 5 % of the samples and 11 % of the stations; <br />largemouth bass, 7% and 19%; white sucker, 8% and <br />13 %; and yellow perch, 3 % and 8 %. Collectively, these <br />five species represented 45 % of the 620 samples analyzed. <br />The proportional representation of the five major species <br />was lower than reported for 1970-74; consequently, the <br />data set was even more heterogeneous than before, and <br />additional species Were numerous. Other frequently col- <br />lected species for the period 1976-79 included smallmouth <br />buffalo, largescale sucker, walleye, lake trout, bloater, and <br />white catfish. When the data set was reduced to the 102 <br />stations with continuous data from 1976 through 1979, <br />there were 54 taxa; when it was trimmed further to 78 sta- <br />tions and the 1974 data were added, there were 52 taxa. <br />The proportional representation of the five major species <br />in the three data sets was nearly identical; collectively, they <br />represented 45% of the total 1976-79 samples, 44% of the <br />samples in the 102-station subset (1976-79), and 46%0 of <br />the 78-station subset (1974-79). Conclusions regarding <br />temporal trends that are drawn from all the data or from <br />either subset should therefore not be overly biased by dif- <br />ferences in the proportional species composition of the data <br />sets. <br />Year-to-year continuity at the stations declined slightly <br />compared with that reported for 1970-74 (Schmitt et al. <br />1981). At the 102 stations for which data are available for <br />both 1976-77 and 1978-79, one species was common to both <br />collections at 79 stations (78%); two or more identical <br />species were collected in both periods at 44 stations (43%); <br />and three identical species were taken in both collection <br />periods at one station (No. 115). For the 78-station subset <br />spanning three collection periods (1974, 1976-77, and <br />1978-79), continuity was poorer: At 46 stations (59%) one <br />species was common to all three collection periods; at 16 <br />stations (20%) there were two such species; and at no sta- <br />tions were three species common to all three collection