The effects of the three Gorges Dam's (TGD's) experimental impoundment on the phytoplankton community in the Xiangxi River, China

被引:21
作者
Bi Y. [1 ]
Zhu K. [1 ,2 ]
Hu Z. [1 ]
Zhang L. [1 ,2 ]
Yu B. [1 ]
Zhang Q. [1 ]
机构
[1] State Key Laboratory of Freshwater Ecology and Biotechnology, Institute of Hydrobiology, Chinese Academy of Science
[2] Graduate University of Chinese Academy of Science
关键词
Impoundment; Phytoplankton community; The three gorges dam (TGD); The three gorges reservoir (TGR);
D O I
10.1080/00207231003704196
中图分类号
学科分类号
摘要
The experimental impoundment of the Three Gorges Dam (TGD) on phytoplankton community was conducted in 2008. Before the impoundment, the phytoplankton comprised various taxa including Bacillariophyta, Chlorophyta, Cryptophyta, Dinophyta and Cyanophyta. While Chlorophyta contributed considerable taxa, numerically, diatom constituted the main component. Cell density was 1.83~7.78 × 106 ind/L: biomass was 3.62~8.89 μg/L; total phosphorus (TP) and total nitrogen (TN) were 0.101~0.233 mg/L and 1.367~2.596 mg/L, respectively. During the impoundment, some species disappeared, leaving diatom dominant. Cell density and biomass decreased significantly (p < 0.05) and pH and TP decreased; but, dissolved oxygen (DO) and TN increased. Remarkable spatial (horizontal and vertical) (p < 0.05) as well as temporal variations were recorded in the distribution of phytoplankton. Temporal effects included changes in the phytoplankton community and nutrient concentration due to dilution and enrichment by the inputting water. © 2010 Taylor & Francis.
引用
收藏
页码:207 / 221
页数:14
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共 40 条
  • [1] Walker K.F., A review of the ecological effects of river regulation in Australia, Hydrobiologia, 125, pp. 111-129, (1985)
  • [2] Dynesius M., Nilsson C., Fragmentation and flow regulation of river systems in the northern third of the world, Science, 266, pp. 753-762, (1994)
  • [3] Power M.E., Sun A., Parker G., Dietrich W.E., Wootton J.T., Hydraulic food chain models, Bioscience, 45, pp. 159-167, (1995)
  • [4] Power M.E., Dietrich W.E., Finlay J.C., Dams and downstream aquatic biodiversity: Potential food web consequences of hydrologic and geomorphic change, Environmental Management, 20, pp. 887-895, (1996)
  • [5] Mullan J.W., Starostka V.J., Stone J.L., Wiley R.W., Wihzius W.J., Factors Affecting Upper Colorado River Reservoir Tailwater Trout Fisheries, (1976)
  • [6] Stanford J.A., Ward J.V., Reservoirs of the Colorado system, The Ecology of River Systems, pp. 374-383, (1986)
  • [7] de Merona B., Albert P., Ecological monitoring of fish assemblages downstream of a hydroelectric dam in French Guiana (South America), Regulated Rivers: Research & Management, 15, pp. 339-351, (1999)
  • [8] Paragamian V.L., Changes in the species composition of the fish community in a reach of the Kootenai River, Idaho, after construction of Libby Dam, Journal of Freshwater Ecology, 17, pp. 375-383, (2002)
  • [9] Poff N.L., Hart D.D., How dams vary and why it matters for the emerging science of dam removal, Bioscience, 52, pp. 659-668, (2002)
  • [10] Preece R.M., Jones H.A., The effect of Keepit Dam on the temperature regime of the Namoi River, Australia, River Research and Applications, 18, pp. 397-414, (2002)