Macrobenthic community structure before, during, and after implementation of the Clean Water Act in the Neches River estuary (Texas)
Community structure of macrobenthos in the industrialized, tidal Neches River was studied 12 years after implementation of phase III of the Clean Water Act (CWA). Result were compared with a 1971-72 study conducted before implementation of the CWA and a 1984-85 study conducted after implementation o...
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Published in | Hydrobiologia Vol. 474; no. 1-3; pp. 213 - 222 |
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Main Authors | , |
Format | Journal Article |
Language | English |
Published |
Dordrecht
Springer
01.04.2002
Springer Nature B.V |
Subjects | |
Online Access | Get full text |
ISSN | 0018-8158 1573-5117 |
DOI | 10.1023/A:1016596123558 |
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Abstract | Community structure of macrobenthos in the industrialized, tidal Neches River was studied 12 years after implementation of phase III of the Clean Water Act (CWA). Result were compared with a 1971-72 study conducted before implementation of the CWA and a 1984-85 study conducted after implementation of phases I & II of the CWA. The permitted BOD waste load decreased 93% between the 1971-72 and 1984-85 studies, then increased 19% between 1984-85 and the current study. A total of 50 taxa were collected during the 1971-72 study, 104 during the 1984-85 study, and 110 during the current study. Numbers of taxa per collection at each station increased by a factor of at least two between the 1971-72 and 1984-85 studies and were significantly different at the 0.0001 level. Numbers of taxa per collection at each station were not significantly different between the 1984-85 and the current study (p=0.286). Minimum collection densities in 1984-85 were higher than maximum densities in 1971-72 and were significantly different at the 0.0001 level. Collection densities were not significantly different between the 1984-85 study and the current study (p=0.374). Shannon's annual and station collection diversity values significantly increased (p=<0.05) between the 1971-72 and 1984-85 studies, but not between the 1984-85 and the current study (p=>0.05). Dendrograms of Sorenson's similarity index between all pairs of stations were more alike between the 1971-72 and the current study than between the 1984-85 and the current study. Evidence of some organic enrichment at the upper stations was indicated by the dominance of Limnodrilus hoffmeisteri and depressed oxygen concentrations. Environmental quality in the river has greatly improved since implementation of the CWA in 1972. Most of the improvments were due to phases I & II of the CWA, with little apparent change since implementation of phase III.[PUBLICATION ABSTRACT] |
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AbstractList | Community structure of macrobenthos in the industrialized, tidal Neches River was studied 12 years after implementation of phase III of the Clean Water Act (CWA). Result were compared with a 1971-72 study conducted before implementation of the CWA and a 1984-85 study conducted after implementation of phases I & II of the CWA. The permitted BOD waste load decreased 93% between the 1971-72 and 1984-85 studies, then increased 19% between 1984-85 and the current study. A total of 50 taxa were collected during the 1971-72 study, 104 during the 1984-85 study, and 110 during the current study. Numbers of taxa per collection at each station increased by a factor of at least two between the 1971-72 and 1984-85 studies and were significantly different at the 0.0001 level. Numbers of taxa per collection at each station were not significantly different between the 1984-85 and the current study (p=0.286). Minimum collection densities in 1984-85 were higher than maximum densities in 1971-72 and were significantly different at the 0.0001 level. Collection densities were not significantly different between the 1984-85 study and the current study (p=0.374). Shannon's annual and station collection diversity values significantly increased (p= < 0.05) between the 1971-72 and 1984-85 studies, but not between the 1984-85 and the current study (p= > 0.05). Dendrograms of Sorenson's similarity index between all pairs of stations were more alike between the 1971-72 and the current study than between the 1984-85 and the current study. Evidence of some organic enrichment at the upper stations was indicated by the dominance of Limnodrilus hoffmeisteri and depressed oxygen concentrations. Environmental quality in the river has greatly improved since implementation of the CWA in 1972. Most of the improvments were due to phases I & II of the CWA, with little apparent change since implementation of phase III. The tidal Neches River, TX, channelized and highly polluted from industrial activity, was the subject of Clean Water Act action. Macrobenthos community structure in the river was studied in 1971-2 before the cleanup, then in 1984-5 after two phases of cleanup, then again 12 yr after the third phase of the cleanup action. BOD waste load declined 93% by the second study, then increased 19% between the second and third surveys. Numbers of taxa collected increased with each successive study. Results for numbers of taxa per collection at each station, collection densities, collection diversity, and other indicators also are reported, generally showing major improvement between the first and second studies and either less improvement or no significant change after the third phase was implemented. Environmental quality in the river has improved greatly since the Clean Water Act was first implemented in 1972. Community structure of macrobenthos in the industrialized, tidal Neches River was studied 12 years after implementation of phase III of the Clean Water Act (CWA). Result were compared with a 1971-72 study conducted before implementation of the CWA and a 1984-85 study conducted after implementation of phases I & II of the CWA. The permitted BOD waste load decreased 93% between the 1971-72 and 1984-85 studies, then increased 19% between 1984-85 and the current study. A total of 50 taxa were collected during the 1971-72 study, 104 during the 1984-85 study, and 110 during the current study. Numbers of taxa per collection at each station increased by a factor of at least two between the 1971-72 and 1984-85 studies and were significantly different at the 0.0001 level. Numbers of taxa per collection at each station were not significantly different between the 1984-85 and the current study (p=0.286). Minimum collection densities in 1984-85 were higher than maximum densities in 1971-72 and were significantly different at the 0.0001 level. Collection densities were not significantly different between the 1984-85 study and the current study (p=0.374). Shannon's annual and station collection diversity values significantly increased (p=<0.05) between the 1971-72 and 1984-85 studies, but not between the 1984-85 and the current study (p=>0.05). Dendrograms of Sorenson's similarity index between all pairs of stations were more alike between the 1971-72 and the current study than between the 1984-85 and the current study. Evidence of some organic enrichment at the upper stations was indicated by the dominance of Limnodrilus hoffmeisteri and depressed oxygen concentrations. Environmental quality in the river has greatly improved since implementation of the CWA in 1972. Most of the improvments were due to phases I & II of the CWA, with little apparent change since implementation of phase III.[PUBLICATION ABSTRACT] |
Author | Smith, Shawn T. Harrel, Richard C. |
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Cites_doi | 10.1126/science.235.4796.1607 10.2307/1351860 10.1007/BF00008537 10.2307/1294272 |
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References | R. A. Smith (405048_CR17) 1987; 235 Environmental Protection Agency (405048_CR4) 1980 H. L. Alder (405048_CR2) 1972 Texas Department of Water Resources (405048_CR20) 1978 S. Warshaw (405048_CR24) 1974 R. C. Harrel (405048_CR8) 1993; 10 T. Sorenson (405048_CR19) 1948; 5 C. J. Krebs (405048_CR11) 1989 R. C. Harrel (405048_CR7) 1991; 211 M. A. McConnell (405048_CR13) 1995; 11 A. F. Holland (405048_CR10) 1985; 8 405048_CR21 Lower Neches Valley Authority (405048_CR12) 1961 U.S. Army Corps of Engineers (405048_CR23) 1981 R. C. Harrel (405048_CR5) 1975; 26 S. R. Twidwell (405048_CR22) 1986 R. Patrick (405048_CR14) 1992 R. C. Harrel (405048_CR6) 1976; 20 B. C. Patten (405048_CR15) 1962; 20 R. R. Sokal (405048_CR18) 1969 C. E. Shannon (405048_CR16) 1949 405048_CR1 J. R. Davis (405048_CR3) 1984 J. L. Wilhm (405048_CR25) 1968; 18 R. C. Harrel (405048_CR9) 1995; 18 |
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Snippet | Community structure of macrobenthos in the industrialized, tidal Neches River was studied 12 years after implementation of phase III of the Clean Water Act... The tidal Neches River, TX, channelized and highly polluted from industrial activity, was the subject of Clean Water Act action. Macrobenthos community... |
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SubjectTerms | Animal and plant ecology Animal, plant and microbial ecology Applied ecology Biochemical oxygen demand Biological and medical sciences Brackish Clean Water Act-US Community structure Conservation, protection and management of environment and wildlife Environmental degradation: ecosystems survey and restoration Environmental law Environmental protection Environmental quality Estuaries Fresh water ecosystems Freshwater Fundamental and applied biological sciences. Psychology Limnodrilus hoffmeisteri Rivers Studies Synecology USA, Texas, Neches Estuary Waste load |
Title | Macrobenthic community structure before, during, and after implementation of the Clean Water Act in the Neches River estuary (Texas) |
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