阿什河流域地下水脆弱性分区

为识别阿什河流域地下水易污区,基于DRASTIC模型,结合研究区水文地质特点和地下水源地特质,舍弃土壤类型和水力传导系数指标,新增抽水井群影响范围评价指标,得到适用于阿什河流域的DRATIE脆弱性评价体系.借助OpenGeoSys(OGS)软件,模拟研究区抽水与不抽水时的地下水流场,圈划出抽水时流场的变化区域,划分抽水井群影响范围.运用DRATIE模型对研究区进行脆弱性评价,绘制研究区地下水脆弱性分区图,并根据用水趋势进行脆弱性情景分析.结果表明:研究区地下水脆弱性主要为较低、中、较高3个级别;河漫滩和阶地区域较易受到污染,抽水井群影响范围内脆弱性为中等,1号井群每口井抽水量不宜超过3.23×10-2 m3/s,2号井群每口井抽水量不宜超过4.00×10-2 m3/s;其余地区较不易受到污染.研究显示,应严格控制水源地抽水量,以防阿什河水体倒灌;合理分配1、2号井群抽水量,可减小水源地脆弱性范围和等级.      

The importance of chemical buffering for pelagic and benthic colonization in acidic waters

In poorly buffered areas acidification may occur for two reasons: through atmospheric deposition of acidifying substances and – in mining districts – through pyrite weathering. These different sources of acidity lead to distinct clearly geochemistry in lakes and rivers. In general, the geochemistry is the major determinant for the planktonic composition of the acidified water bodies, whereas the nutrient status mainly determines the level of biomass. A number of acidic mining lakes in Eastern Germany have to be neutralized to meet the water quality goals of the European Union Directives and to overcome the ecological degradation. This neutralization process is limnologically a short-term maturation of lakes, which permits biological succession to overcome two different geochemical buffer systems. First, the iron buffer system characterizes an initial state, when colonization starts: there is low organismic diversity and productivity, clear net heterotrophy in most cases. Organic carbon that serves as fuel for the food web derives mainly from allochthonous sources. In the second, less acidic state aluminum is the buffer. This state is found exceptionally among the hard water mining lakes, often as a result of deposition of acidifying substances onto soft water systems. Colonization in aluminum-buffered lakes is more complex and controlled by the sensitivity of the organisms towards both, protons and inorganic reactive aluminum species. In soft-water systems, calcium may act as antidote against acid and aluminum; however, this function is lost in hard water post mining lakes of similar proton concentrations. Nutrient limitations may occur, but these do not usually control qualitative and quantitative plankton composition. In these lakes, total pelagic biomass is controlled by the bioavailability of nutrients, particularly phosphorus.