Temporal Variability of Fauna in the Same Areas

The variability of the population in successive collections from the same area is presented in Table 14. Supplementary data obtained in Areas 2, 4 and 7 support conclusions discussed below for Areas 1, 3 and 6. The abundance of some species maintained a constant level, whereas that of others varied.

Table 14. Numbers of Individuals Collected by Means of the Shocker at Varying Intervals in September, 1959. The Number at the Top of Each Column is the Date When the Collection was Made.

SpeciesArea 1Area 3Area 6
34891015161820
Golden Redhorse 2 2 ... 5 5 2 ... ... 3
Creek Chub 4 3 7 1 ... ... 1 2 ...
Sucker-mouthed Minnow ... ... ... 54 42 25 31 7 6
Red-finned Shiner ... ... 1 ... ... 4 31 13 4
Red Shiner 44 7 211 117 170 438 186 209 62
Blunt-nosed Minnow ... ... ... 4 10 19 108 91 13
Fat-headed Minnow 1 ... ... 1 2 3 112 156 48
Stoneroller 67 39 49 84 107 55 54 67 22
Black Bullhead 5 ... 1 2 1 ... ... 3 7
Yellow Bullhead 1 1 ... 2 1 ... 1 ... 3
Channel Catfish 14 7 ... 36 16 ... 3 1 23
Channel Catfish(yy)[H] 23 16 17 34 34 22 40 23 28
Flathead ... ... ... 4 8 1 2 ... 1
Flathead(yy) 4 1 1 2 1 1 ... ... ...
Stonecat 25 8 12 7 7 5 ... ... ...
Green Sunfish 27 17 12 13 16 17 62 62 74
Long-eared Sunfish 13 12 1 6 3 3 10 22 31
Logperch 1 ... ... 2 ... ... ... ... ...
Slender-headed Darter ... 1 2 55 45 23 15 1 1
Orange-throated Darter 2 1 2 9 11 8 5 ... 1
Total 233 115 316 438 480 626 661 657 347

Stoneroller, channel catfish (young-of-the-year), green sunfish, and long-eared sunfish formed the most stable element of the population, in that the numbers of these species varied less in successive collections than did numbers of other species.

The number of orange-throated darters remained constant at Areas 1 and 3, and the number of stonecats changed little in successive collections from Area 3. I suspect that an apparent decline in stonecats at Area 1 on September 4 was due to a slow rate of dispersal from the point of release (see pages 413, 414).

Some species (sucker-mouthed minnow, red-finned shiner, slender-headed darter, and fat-headed minnow) decreased significantly in successive samples from the same area because of mortality in handling or movement out of the area of initial capture.

The decrease in abundance of the sucker-mouthed minnow may have been due to some mobility of the species. Evidence for mortality caused by handling was obtained for the red-finned shiner and probably accounts for the reduction of this species in Area 6. The red-finned shiner is also probably a mobile species. The reduction in abundance of the slender-headed darter seems unexplainable because no evidence was obtained for either movement or mortality.

Fat-headed minnows also declined markedly in successive collections from Area 6, the only area in which the species was common. No marked fat-headed minnows were taken outside the area of release, indicating low mobility of the species. I cannot certainly account for their decline; possibly there was latent mortality due to shocking.

The numbers of red shiners, blunt-nosed minnows, and juvenile channel catfish varied erratically in successive collections, probably as a result of movement. This problem is discussed for all species in a later section.