<br />716
<br />
<br />A. JOHN GATZ. JR.
<br />
<br />Ecology. Vol. 60, No.4
<br />
<br />centage overlap of r.oexisting species varies within
<br />limits (39-86%) only~bout half as great as those pos-
<br />sible (O-lOV%) and averages nearly the same (64-66%)
<br />in all three streams. Distances between niches in nine-
<br />dimensional space show a consistent pattern (Fig. I)
<br />which is distinguishable from a comparable random
<br />pattern (Fig. 2).
<br />One possible explanation for the patterns observed
<br />is that these fish communities were structured by com-
<br />petition. Competition theory suggests that species too
<br />similar to coexist should either diverge over evolu-
<br />tionary time, or one should be lost from the system.
<br />Similarly, species quite dissimilar might either con-
<br />verge. or the community might be invaded by an in-
<br />termediate form. The net result of these processes
<br />should be a regular spacing of species along those re-
<br />source axes in which competition has been important.
<br />As Schoener (1974) has summarized, complementarity
<br />in separation along axes of several dimensions has
<br />often been found. Such complementarity could be pro-
<br />duced by competition exerting an influence along some
<br />axes but not others. In such a case, we might expect
<br />the overall distribution pattern of distances between
<br />niches observed in nature to be similar to a hypothet-
<br />ical one produced by placing species at regular inter-
<br />vals along some resource axes and at random positions
<br />along others. I modeled such communities and the re-
<br />sulting distributions of distances in N-dimensional
<br />space were similar to those that I actually observed in
<br />nature. That is, larger and smaller distances between
<br />niches were more abundant in model communities and
<br />in nature than in the randomly assembled communi-
<br />ties. Competition along some. but not all, niche di-
<br />mensions over evolutionary time can thus be offered
<br />as a possibk explanation for this pattern. However,
<br />the fact that my data agree with the predictions of
<br />competition theory is no proof that the observed pat-
<br />terns were produced by competition. Alternative hy-
<br />potheses. to be proved or disproved. must be consid-
<br />ered wherever possiblt:.
<br />One instance in which a testable alternative hypoth-
<br />esis can be considered pertains to the pattern seen in
<br />Fig. I. Perhaps the principal characteristic of the ob-
<br />served niche-spacing pattern is that there exists an
<br />excess of small distances relative to the random pat-
<br />tern. That is, clusters of species exist. An obvious
<br />possible explanation would be one relating to phylog-
<br />eny: species closely related to each other might be
<br />expected to cluster with one another and to be distant
<br />from less closely related species. This possibility is
<br />especially worthy of consideration in that the niches
<br />were defined morphologically in the first place. Mor-
<br />phologically similar species are likely also to be close
<br />both phylogenetically and taxonomically. I initially
<br />examined this possible explanation of the pattern by
<br />scanning the matrices of Euclidean distances. Many
<br />of the very small distances are. in fact. between two
<br />species within a single family. However, this is by no
<br />
<br />means always the case. For example, in Maho Creek
<br />Phoxinus oreas, the mountain red belly dace. is closer
<br />to Erimyzon oblongus, the creek chubsucker, than to
<br />any of the other eight members of its own family; Per-
<br />ea fiaveseens, the yellow perch, is more similar to
<br />several sunfishes (Lepomis (Iud/us, L. eyanellus, L.
<br />gibbosus. and L. gUlOSllS) than it is to its two fellow
<br />Percidae.
<br />In order to consider this same question in a more
<br />objective manner, I tested some additional hypothe-
<br />ses. I compared the distribution of distances between
<br />sympatrically occurring members of a single family or
<br />genus with the distance distribution which was ob-
<br />tained using the same number of random niches. Spe-
<br />cifically, I used: (I) all species of cyprinids (minnows)
<br />sympatric in Maho Creek: (2) all species of centrar-
<br />chids (sunfishes and basses) sympatric in Mud Creek;
<br />(3) all species of No/ropis (shiners) sympatric in Maho
<br />Creek; and (4) all species of Lepomis (sunfishes) sym-
<br />patric in both Mud and Maho Creek. In all four of
<br />these cases, the results were similar to those for the
<br />entire ichthyofaunal assemblages. The distances be-
<br />tween the morphologically defined niches of species
<br />at any given level of ta,'<.onomic relatedness showed
<br />more small values and more large values than would
<br />be expected given a random position on each niche
<br />axis. Thus deviation from randomness does not seem
<br />to be a taxonomic artifact. The evolution of niche
<br />spacing of these coexisting fish species seems to be
<br />nonrandom no matter what level of taxon is used.
<br />A structure similar to that observed here would not
<br />be produced by other phenomena (e.g., predation,
<br />symbiosis or physical factors) which have been sU'g-
<br />gested as possible bases for community organization:
<br />hence no particular hypotheses have been tested. [
<br />tentatively conclude. therefore, that competition was
<br />the most likely agent whereby evolution has produced
<br />the patterns identified above. By examining the pat-
<br />tern of spacing between each pair of niche centers I
<br />am assuming that diffuse competition exists, i.e., each
<br />species has competitive interactions with every other
<br />species. While previous field studies on communities
<br />of fishes have shown high degrees of interaction
<br />among large numbers of species (Hartley 1948, Star-
<br />rett 1950, Keast 1965. /966, Keast and Webb 1966).
<br />none of these investigators nor I intend to suggest that
<br />every possible interaction is of equal competitive im-
<br />portanc(. However, my assumption of diffuse com-
<br />petition seems more realistic than the primary alter-
<br />native: considering spacing only between those pairs
<br />of species which are most similar to each other.
<br />Other workers have previously reported on the re-
<br />lationship between total niche space and number of
<br />species, and their results vary considerably. Schoener
<br />(1974) suggested that the total amount of niche space
<br />occupied should increase as a function of the number
<br />of species present. Brown (1975) reported that niche
<br />overlap increased to a maximum as number of species
<br />
<br />!1.:
<br />t
<br />:1-
<br />~
<br />$
<br />j
<br />
<br />
<br />August 1979
<br />
<br />COMMUNITY ORGANIZATION IN FISHES
<br />
<br />717
<br />
<br />of sympatric desert rodents went from two to five or six.
<br />But Brown (1975) also noted that these results were
<br />based on only two aspects of the niche, seed size and for-
<br />aging site. and hence may differ if more factors were
<br />considered. Pianka (1975) reported the opposite result
<br />for his desert lizards. Using measures of niche breadth
<br />in food, habitat, and time dimensions, he found that
<br />species packing actually decreased as number of
<br />species increased. As Pianka (1975) suggests. this re-
<br />sult would be expected if niche overlap were a func-
<br />tion of the amount of diffuse competition. This same
<br />tendency toward looser packing in the tropics than in
<br />temperate regions was also found by Findley (1976) in
<br />his study on the eco-morphology of 220 bat species.
<br />This conclusion contrasts with his earlier result using
<br />a different set of bat species (Findley 1973) in which
<br />he found that increased species numbers sometimes
<br />were and sometimes were not accompanied by in-
<br />creased species packing. Karr and James (1975) re-
<br />ported different results depending on what sets of mor-
<br />phological indices they used. On the one hand, they
<br />found that morphological space with regard to wing
<br />and tarsal measurements was larger in the species-rich
<br />tropics compared to the data obtained from a temper-
<br />ate site, but species packing remained constant. Con-
<br />versely, they found that species packing increased in
<br />the tropics when only bill dimensions were consid-
<br />ered. Ricklefs and O'Rourke (1975) reported that
<br />species packing did not change as number of moth
<br />species increased.
<br />Certainly it is possible that different faunas could
<br />show different relationships between species packing
<br />and number as the results cited above imply. But at
<br />the same time, the great variety of methods used in
<br />these studies might themselves be expected to produce
<br />many differences in results. In particular. not aU in-
<br />vestigations actually dealt with complete deSCriptions
<br />of the niche. Brown (1975) did not. and Karr and
<br />James (1975) fragmented even the amount of morpho-
<br />logical space they were studying. Although Findley's
<br />(1973) results suggest that characteristics of faunal
<br />packing may vary even within a taxon, they are based
<br />on questionable measures of packing and phenetic di-
<br />versity (see Gatz, in press). A critical assessment of
<br />technique is definitely in order before the results of
<br />any of the studies cited, or the present one, are ac-
<br />cepted or generalized.
<br />
<br />ACKNOWLEDGMENTS
<br />
<br />I thank especially J. G. Lundberg. D. A. LivingslOne. and
<br />S. A. Wainwright for advice during the course of this re-
<br />search and J. B. Leverenz. T. C. Cowles. and J. G. Lundberg
<br />for assistance in the collection of fishes. I thank John G.
<br />Lundberg. Wendell K. Patton. Eric P. Pianka. Dennis C.
<br />Radabaugh. Daniell. Rubenstein, and Henry M. Wilbur for
<br />critical commentary on the ideas and work presented.
<br />The research was partially supported by a Cocos Foun-
<br />dation Training Grant in Morphology to the author and was
<br />conducted in partial fulfillment of the requirements for the
<br />Ph.D. at Duke University.
<br />
<br />LiTERATURE CITEO
<br />
<br />Aleev. Yu. G. 1969. Function and gross morphology in fish.
<br />Israel Program for Scientific Translations, Jerusalem, is-
<br />rael.
<br />Andrusak, H., and T. G. Northcote. 197\. Segregation be-
<br />tween adult cutthroat trout (Salmo clarki) and Dolly Var-
<br />den (Salvetinus malma) in small coastal British Columbia
<br />lakes. Journal of the Fisheries Research Board of Canada
<br />28: 1259-1268.
<br />Brown, J. H. 1975. Geographical ecology of desert rodents.
<br />Pages 3l5-34l in M. L. Cody and J. M. Diamond, editors.
<br />Ecology and evolution of communities. The Belknap Press
<br />of Harvard University Press. Cambridge, Massachusetts,
<br />USA.
<br />Findley, J. S. 1973. Phenetic packing as a measure of faunal
<br />diversity. American Naturalist 107:580-584.
<br />-. 1976. The structure of bat communities. American
<br />Naturalist 110: 129-139.
<br />Gatz, A. J. Jr. 1979. Ecological morphology of freshwater
<br />stream fishes. Tulane Studies in Zoology and Botany
<br />21:91-124.
<br />-. in press. Phenetic packing and community struc-
<br />ture: a methodological comment. American Naturalist.
<br />Griffith, J. S. Jr. 1974. Utilization of invertebrate drift by
<br />brook trout (Salvetinus fon/inatis) and cutthroat trout (Sal-
<br />mo clarki) in small streams in Idaho. Transactions of the
<br />American Fisheries Society 103:440-447.
<br />Hanley. P. H. T. t948. Food and feeding relationships in a
<br />community of freshwater fishes. Journal of Animal Ecol-
<br />ogy 17: 1-14.
<br />Hutchinson. G. E. 1957. Concluding remarks. Cold Spring
<br />Harbor Symposia on Quantitative Biology 22:415-427.
<br />-. 1968. When are species necessary? Pages 177-186
<br />in R. C. Lewontin. editor. Population biology and evolu-
<br />tion. Syracuse University Press. Syracuse, New York,
<br />USA.
<br />Karr. J. R.. and F. C. James. 1975. Eco-morphological con-
<br />figurations and convergem evolution in species and com.
<br />munities. Pages 258-291 in M. L. Cody and J. M. Dia-
<br />mond, editors. Ecology and evolution of communities. The
<br />Belknap Press of Harvard University Press. Cambridge.
<br />Massachusetts. USA.
<br />Keast. A. 1965. Resource subdivision amongst cohabiting
<br />fish species in a bay. Lake Opinicon. Ontario. University
<br />of Michigan. Great Lakes Research Division ""blication
<br />Number 13: 106-132.
<br />-. 1966. Trophic interrelationships in the fish fauna of
<br />a small stream. University of Michigan, Great Lakes Re-
<br />search Division Publication Number 15:5/-79.
<br />Keast, A., and D. Webb. 1966. Mouth and body form rel-
<br />ative to feeding ecology in the fish fauna of a small lake,
<br />Lake Opinicon. Ontario. Journal of the Fisheries Research
<br />Board of Canada 23: 1845-1874.
<br />Krebs. C. J. 1978. Ecology: the e.perimental analysis of
<br />distribution and abundance. Second edition. Harper and
<br />Row. New York. New York, USA.
<br />Nikolskii, G. V. 1933. On the intluence of the rate of tlow
<br />on the fish fauna of the rivers of central Asia. Journal of
<br />Animal Ecology 2:266-281.
<br />Nilsson. N.-A. 1955. Studies on the feeding habits of trout
<br />and char in north Swedish lakes. Reports of the Institute
<br />of Freshwater Research, Drottningholm 36: 163-225.
<br />-. 1960. Seasonal tluctuations in the food segregation
<br />of trout. char and whitefish in fourteen north-Swedish
<br />lakes. Reports of the Institute of Freshwater Research.
<br />Drottningholm 41: 185-205.
<br />-. 1963. Interaction between trout and char in Scan-
<br />dinavia. Transactions of the American Fisheries Society
<br />92:276-285.
<br />-. 1965. Food segregation between salmonid species
<br />
|