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  • Ceriodaphnia  (1)
  • Fish community structure  (1)
  • 1
    Electronic Resource
    Electronic Resource
    Springer
    Oecologia 87 (1991), S. 336-342 
    ISSN: 1432-1939
    Keywords: Fish ; Fish community structure ; Habitat selection ; Headwater streams ; Predation risk
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Summary Surveys of 262 pools in 3 small streams in eastern Tennessee demonstrated a strong positive relationship between pool depth and the size of the largest fish within a pool (P〈0.001). Similarly, the largest colonizers of newly-created deep pools were larger than the colonizers of shallow pools. We explored the role of predation risk in contributing to the “bigger fish — deeper habitat” pattern, which has been noted by others, by conducting five manipulative field experiments in two streams. Three experiments used stoneroller minnows (Campostoma anomalum); one used creek chubs (Semotilus atromaculatus); and one used striped shiners (Notropis chrysocephalus). The stoneroller experiments showed that survival of fish approximately 100 mm in total length (TL) was much lower in shallow pools (10 cm deep) than in deep (40 cm maximum) pools (19% versus 80% survival over 12 d in one experiment) and added cover markedly increased stoneroller survival in shallow pools (from 49% to 96% in an 11-d experiment). The creek chub experiment showed that, as for stonerollers, pool depth markedly influenced survival: the chubs survived an average of 4.9 d in shallow pools and 〉10.8 d in deep pools. In the striped shiner experiment in shallow artificial streamside troughs, no individuals 75–100 mm TL survived as long as 13 d, where-as smaller (20–25 mm) fish had 100% survival over 13 d. The results of the experiments show that predation risk from wading/diving animals (e.g., herons and raccoons) is much higher for larger fishes in shallow water than for these fishes in deeper water or for smaller fish in shallow water. We discuss the role of predation risk from two sources (piscivorous fish, which are more effective in deeper habitats, and diving/wading predators, which are more effective in shallow habitats) in contributing to the bigger fish — deeper habitat pattern in streams.
    Type of Medium: Electronic Resource
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  • 2
    Electronic Resource
    Electronic Resource
    Springer
    Ecotoxicology 5 (1996), S. 377-393 
    ISSN: 1573-3017
    Keywords: ambient toxicity testing ; Ceriodaphnia ; fathead minnow larvae ; biological monitoring
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract The purpose of this paper is to show how short-term laboratory tests, conducted according to US Environmental Protection Agency (EPA) procedures, can be used effectively to assess water-quality conditions in streams or rivers that receive pollutants from industry or municipal or agricultural areas. Standardized, short-term tests with fish, aquatic invertebrates or algae are commonly used to estimate the acute or chronic toxicity of wastewaters; this is referred to as effuent testing. The methods used for testing effluents also can be used to assess water quality in receiving streams: in this application, the procedures are referred to as ambient testing. Despite similarity in methods, the major objective of effluent testing differs importantly from that of ambient testing. In effluent testing, the key objective is to determine how toxic an effluent is; in ambient testing, the main objective usually is that of determining if the water at a site is toxic. This difference is subtle but very important: it shapes the strategy for cost-effective ambient testing, and determines the framework for effective statistical analysis and interpretation of ambient toxicity test results. Specific case-study examples are provided demonstrating the kinds of information that can be extracted from ambient toxicity testing by use of different statistical methods, including analysis of variance, contingency-table analysis, and two types of multivariate procedures (principal components analysis and logistic regression). Examples also are given supporting the idea that an effective ambient testing programme should be long-term, and contain a diagnostic-testing component analogous to the toxicity identification procedures used to supplement effluent-testing programmes. Recommendations derived as ‘lessons learned’ from largescale ambient toxicity testing programmes for receiving streams at Department of Energy facilities include: (1) testing more frequently with one species (preferably Ceriodaphnia) generally is more effective, in terms of information gained per dollar spent, than testing less frequently with two or more species; (2) use five or more sites per test period, plus two or more reference sites, whenever possible; (3) use four to six test periods per year; and (4) use diagnostic testing to supplement the ambient-testing programme. Various laboratory and in situ methods for environmental assessment are now under development, but these methods probably will not gain acceptance for use in regulatory situations for many years. Rapid growth in need for ecological risk assessments outstrips the rate at which new test procedures are approved for regulatory purposes. Thus, laboratory tests for estimating possible environmental impacts of toxic or disruptive pollutants are likely to be used more frequently during the next decade.
    Type of Medium: Electronic Resource
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