Widespread omnivory and low temporal and spatial variation in the diet of fishes in a hydrologically variable northern Australian river.

This article examines the trophic ecology of freshwater fishes (22 species in 15 families) in a wet and dry tropical Australian river of high intra-annual and interannual hydrological variability. Seven major trophic groups were identified by cluster analysis; however, four food items (filamentous algae, chironomid larvae, Trichoptera larvae and Ephemeroptera nymphs) comprised almost half of the average diet of all species. The influence of species, fish size, spatial effects and temporal effects on food use was investigated using redundancy analysis. Size, time and space accounted for little of the perceived variation. Ontogenetic changes in diet were minor and limited to a few large species. Spatial variation in trophic composition of the fish assemblages reflected the effects of the Burdekin Falls and dam, a major geographic barrier, on species distributions. Little spatial variation in diet was detected after accounting for this biogeographical effect. Temporal variations in flow, although marked, had little effect on variations in fish diet composition due to the low temporal diversity of food resources in physically monotonous sand and gravel channels. Species identity accounted for<50% of the observed variation in food choice; omnivory and generalism were pronounced. The aquatic food web of the Burdekin River appears simple, supported largely by autochthonous production (filamentous and benthic microalgae, and to some extent, aquatic macrophytes). Allochthonous food resources appear to be unimportant. The generalist feeding strategies, widespread omnivory and absence of pronounced trophic segregation reported here for Burdekin River fishes may be common to variable and intermittent rivers of subtropical and tropical northern Australia with similar fish communities and may be a general feature of rivers of low habitat diversity and characterized by flow regimes that vary greatly both within and between years.

The effects of a pulsed application of chlorpyrifos on macroinvertebrate communities in an outdoor artificial stream system.

The results of an experiment examining the effects of pulsed application of a pesticide, chlorpyrifos, in an outdoor replicated artificial stream system are described. Two levels of chlorpyrifos were used, 0.1 microgram.liter-1 (low dose) and 5.0 micrograms.liter-1 (high dose), and applied for 6 hr. Low-dose streams showed little impact from the treatment and were indistinguishable from control streams. Significant reductions in invertebrate density occurred in the high-dose streams and were mainly due to reductions in density of chironomid larvae. There were no significant reductions in taxon richness associated with the treatments indicating no localized extinctions of species. Diversity measures were insensitive to the changes observed in the streams. Ordination and classification procedures were more illuminating and indicated that the major effect of pesticide application was to interfere with the normal pattern of community change occurring within the system. Recovery following treatment was rapid. The results are discussed with reference to the use of indicator species and biological monitoring strategies intended to identify human-mediated disturbance.

An outdoor replicated artificial stream system: design, operating conditions, and initial invertebrate colonization.

The design and operating conditions of an outdoor replicated stream system are described. The facility is composed of a long inlet stream, a header weir which diverts inflowing water to six artificial stream channels (each 45 m long and 40 cm wide), a settlement pond at the end of the channels, and an outlet stream which diverts the water back to an irrigation channel. Flow regulation is achieved by "V-notched" gates at the head of each stream and depth by a second set of gates at the end of each stream. Physicochemical conditions were monitored over a 260-day period and even though significant temporal variation was detected, little between-stream variation was observed for most parameters. Small, but significant, between-stream differences in dissolved oxygen and pH were detected but were attributed to sampling procedure rather than real between-stream differences. A relatively rich invertebrate fauna colonized the streams. Invertebrate densities increased rapidly after initiation of flow and stabilized after 38 days. Chironomoid midge larvae were numerically the most important taxa, although the proportion of total density contributed by this group changed significantly with time. Taxon richness, chironomid taxon richness, diversity, and eveness also increased with time until a stable point was reached after 90 days of flow. No significant between-stream difference in any of these parameters was detected suggesting that colonization dynamics were similar in each stream.

The effects of a chronic application of chlorpyrifos on the macroinvertebrate fauna in an outdoor artificial stream system: species responses.

An outdoor artificial stream system was used to examine the effects of a chronic application of the organophosphate pesticide chlorpyrifos on the invertebrate fauna of the system. Two replicate streams received chlorpyrifos for 21 days at the high dose (5 micrograms.liter-1) or low dose (0.1 microgram.liter-1) or only the carrier solution with which chlorpyrifos is mixed for commercial sale (1,1,1-trichloroethane and xylene). Streams behaved as replicates with respect to five water quality parameters. Seventy-four nonchironomid and 24 chironomid taxa were recorded during the study. The number of taxa and total invertebrate abundance were significantly reduced by both high and low doses of the pesticide. Shannon-Weaver diversity was also reduced by both high and low doses of the pesticide whereas evenness increased in high dose streams. The individual abundances of 9/36 nonchironomid and 13/19 chironomid taxa were significantly reduced by pesticide application; the abundance of one taxon, the gastropod Physastra, increased. The biomass of periphyton in the streams was affected by changes in the abundance of chironomid grazers and Physastra, and the slow recovery of grazers from mortality due to chlorpyrifos appeared to result in a higher biomass of periphyton in the high dose streams than in controls and low dose streams 21 days after dosing ceased. Inverse relationships between the amounts of fine particulate organic matter (FPOM) and the sum of the numbers of all taxa of collector-gatherers (as well as numbers of four individual taxa) were interpreted as disruption of the processing of FPOM by members of this trophic group following toxic effects of chlorpyrifos. The implications of the study for biological monitoring of the direct and indirect effects of chronic doses of chlorpyrifos on streams are discussed, and the use of chironomid larvae and periphyton in biomonitoring to detect pesticide impacts is particularly recommended.