Lin C, Wu Y, Lu W, Chen A, Liu Y
Centre for Ecological and Environmental Technologies, South China Agricultural University, Guangzhou 510642, China.
J Hazard Mater. 2007 Apr 2;142(1-2):199-207. doi: 10.1016/j.jhazmat.2006.08.006. Epub 2006 Aug 12.
Field and laboratory work was carried out to investigate the chemistry and ecotoxicity of stream water affected by acid mine drainage in a tributary catchment of the Pearl River in subtropical China during a major flood that corresponded to a return period of 100 years. The results indicate that stream water was affected by acid mine drainage from the Dabaoshan mine at least to a distance of 25 km downstream of the mine water discharge point. It appears that H(+) generated from sulfide oxidation in the waste rock dumps was readily available for exporting. The amount of H(+) being discharged into the receiving stream depended on the volume of out-flowing waters. However, there was a lag time for the discharges of the metals. This may be attributed to the slower release of metals, relative to H(+), because it might take more time for the dissolution of heavy metal-bearing compounds, particularly the sparsely soluble jarosites. Fe, Zn and Al were the major metals of potential toxicity contained in the AMD-affected stream water, followed by Mn, Cu, Pb, As, Cd and Ni. The concentrations of these metals in the water decreased rapidly down the stream. This corresponds with an increase in the concentrations of reactive heavy metal fractions in benthic mud down the stream, reflecting the precipitation of heavy metal compounds with increasing pH and their subsequent deposition in the streambed. Toxicity tests show that the AMD-affected stream water at 3.5 km downstream of the discharge point was highly toxic to the test organism. At 25 km downstream of the discharge point where stream water pH was as high as 5.75, marked toxic responses of the test organism were still observed.
在中国亚热带地区珠江一条支流集水区发生百年一遇的大洪水期间,开展了野外和实验室工作,以调查受酸性矿山排水影响的溪流水的化学性质和生态毒性。结果表明,溪流水至少在矿井排水点下游25公里的范围内受到大宝山矿酸性矿山排水的影响。废石堆中硫化物氧化产生的H(+)似乎很容易输出。排入接收溪流的H(+)量取决于流出水的体积。然而,金属的排放存在滞后时间。这可能是由于金属的释放比H(+)慢,因为含重金属的化合物,特别是难溶的黄钾铁矾的溶解可能需要更多时间。铁、锌和铝是受酸性矿山排水影响的溪流水所含的主要潜在有毒金属,其次是锰、铜、铅、砷、镉和镍。这些金属在水中的浓度沿溪流迅速降低。这与底泥中活性重金属组分的浓度沿溪流增加相对应,反映了随着pH值升高重金属化合物的沉淀及其随后在河床中的沉积。毒性试验表明,排放点下游3.5公里处受酸性矿山排水影响的溪流水对受试生物具有高毒性。在排放点下游25公里处,溪流水pH值高达5.75,仍观察到受试生物有明显的毒性反应。