USE OF CHIRONOMID DEFORMITIES TO ASSESS ENVIRONMENTAL DEGRADATION IN THE YAMASKA RIVER, QUEBEC

被引:41
作者
BIRD, GA
机构
[1] Environmental Science Branch, AECL Research, Whiteshell Laboratories, Pinawa, R0E 1L0, Manitoba
关键词
D O I
10.1007/BF00545620
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The frequency of morphological deformities in chironomid larvae was used to assess environmental degradation at 12 sites in the Yamaska River, Quebec, that were known to be either impacted by agriculture or urban centres, or were relatively clean and used as reference sites. A total of 2273 chironomid larvae were examined for deformities. The overall frequency of deformities at polluted sites was 2.7%, whereas no deformities were observed at the reference sites. The highest incidence of deformities was found downstream of two urban centres, site 9 at Acton Vale (5.1% deformed) and site 12 at Ste Hyacinthe (5.3% deformed). The frequency of deformities at the agricultural sites ranged from 0.8 to 2.5% and was comparable to sites receiving municipal sewage effluent. The occurrence of higher frequencies of deformities downstream of urban centres indicates that the frequency of deformities increases with environmental degradation.
引用
收藏
页码:163 / 175
页数:13
相关论文
共 27 条
[1]  
Barton D.R., Metcalfe-Smith J.L., A Comparison of Sampling Techniques and Summary Indices for Assessment of Water Quality in the Yamaska River, Quebec, Based on Benthic Macroinvertebrates, Environ. Monit. Assess., 21, pp. 225-244, (1992)
[2]  
Campbell P.G.C., Couture P., Talbot L., Caille A., Nutrient Dynamics in Running Waters: Production, Assimilation and Mineralization of Organic Matter, Environmental Biogeochemistry Vol. 2 Metals Transfer and Ecological Mass Balance, pp. 681-703, (1976)
[3]  
Cushman R.M., Chironomid Deformities as Indicators of Pollution from a Synthetic, Coal-Derived Oil, Freshwater Biol., 14, pp. 179-182, (1984)
[4]  
Day K.E., Metcalfe J.L., Batchelor S.P., Changes in Intercellular Free Amino Acids in Tissues of the Caged Mussel, Elliptio complanata, Exposed to Contaminated Environments, Arch. Environ. Contam. Toxicol., 19, pp. 816-827, (1990)
[5]  
Dermott R.M., Deformities in Larval Procladius spp. and Dominant Chironomini from the St. Clair River, Hydrobiologia, 219, pp. 171-185, (1991)
[6]  
Dickman M., Brindle I., Benson M., Evidence of Teratogens in Sediments of the Niagara River Watershed as Reflected by Chironomid (Diptera: Chironomidae) Deformities, J. Great Lakes Res., 18, pp. 467-480, (1992)
[7]  
Dutka B.J., Kwan K.K., Rao S.S., Jurkovic A., Liu D., River Evaluation Using Ecotoxicological and Microbiological Procedures, Environ. Monit. Assess., 16, pp. 287-313, (1991)
[8]  
Hare L., Carter J.C.H., The Distribution of Chironomus (ss.)? cucini (salinarius Group) Larvae (Diptera: Chironomidae) in Parry Sound, Georgian Bay, with Particular Reference to Structural Deformities, Canadian Journal of Zoology, 54, pp. 2129-2134, (1976)
[9]  
Janssens de Bisthoven L.G.J., Timmermanns K.R., Ollevier F., The Concentration of Cadmium, Lead, Copper and Zinc in Chironomus gr thummi Larvae (Diptera, Chironomidae) with Deformed Versus Normal Mentum, Hydrobiologia, 239, pp. 141-149, (1992)
[10]  
Lan Q., Dickman M., Alvarez M., Evidence of Genotoxic Substances in the Niagara River Watershed, Environ. Toxicol. Wat. Qual., 6, pp. 1-15, (1991)