Sörme L, Lagerkvist R
Department of Water and Environmental Studies, Linköping University, Sweden.
Sci Total Environ. 2002 Oct 21;298(1-3):131-45. doi: 10.1016/s0048-9697(02)00197-3.
The sources of heavy metals to a wastewater treatment plant was investigated. Sources can be actual goods, e.g. runoff from roofs, wear of tires, food, or activities, e.g. large enterprises, car washes. The sources were identified by knowing the metals content in various goods and the emissions from goods to sewage or stormwater. The sources of sewage water and stormwater were categorized to enable comparison with other research and measurements. The categories were households, drainage water, businesses, pipe sediment (all transported in sewage water), atmospheric deposition, traffic, building materials and pipe sediment (transported in stormwater). Results show that it was possible to track the sources of heavy metals for some metals such as Cu and Zn (110 and 100% found, respectively) as well as Ni and Hg (70% found). Other metals sources are still poorly understood or underestimated (Cd 60%, Pb 50%, Cr 20% known). The largest sources of Cu were tap water and roofs. For Zn the largest sources were galvanized material and car washes. In the case of Ni, the largest sources were chemicals used in the WTP and drinking water itself. And finally, for Hg the most dominant emission source was the amalgam in teeth. For Pb, Cr and Cd, where sources were more poorly understood, the largest contributors for all were car washes. Estimated results of sources from this study were compared with previously done measurements. The comparison shows that measured contribution from households is higher than that estimated (except Hg), leading to the conclusion that the sources of sewage water from households are still poorly understood or that known sources are underestimated. In the case of stormwater, the estimated contributions are rather well in agreement with measured contributions, although uncertainties are large for both estimations and measurements. Existing pipe sediments in the plumbing system, which release Hg and Pb, could be one explanation for the missing amount of these metals. Large enterprises were found to make a very small contribution, 4% or less for all metals studied. Smaller enterprises (with the exception of car washes) have been shown to make a small contribution in another city; the contribution in this case study is still unknown.
对一家污水处理厂的重金属来源进行了调查。来源可以是实际物品,如屋顶径流、轮胎磨损、食物,或者活动,如大型企业、洗车行。通过了解各种物品中的金属含量以及物品向污水或雨水的排放来确定来源。对污水和雨水的来源进行了分类,以便与其他研究和测量结果进行比较。分类包括家庭、排水、企业、管道沉积物(全部通过污水输送)、大气沉降、交通、建筑材料和管道沉积物(通过雨水输送)。结果表明,对于某些金属,如铜和锌(分别发现了110%和100%的来源)以及镍和汞(发现了70%的来源),有可能追踪其重金属来源。其他金属来源仍了解不足或被低估(镉60%、铅50%、铬20%已知)。铜的最大来源是自来水和屋顶。锌的最大来源是镀锌材料和洗车行。就镍而言,最大来源是污水处理厂使用的化学品和饮用水本身。最后,汞的最主要排放源是牙齿中的汞合金。对于铅、铬和镉,由于其来源了解较少,所有这些金属的最大贡献者都是洗车行。将本研究的来源估计结果与之前的测量结果进行了比较。比较表明,家庭的测量贡献高于估计值(汞除外),得出的结论是,家庭污水的来源仍了解不足,或者已知来源被低估。对于雨水,估计贡献与测量贡献相当吻合,尽管估计和测量的不确定性都很大。管道系统中现有的管道沉积物会释放汞和铅,这可能是这些金属缺失量的一个解释。发现大型企业的贡献非常小,对所有研究的金属贡献均为4%或更低。在另一个城市,较小的企业(洗车行除外)贡献较小;本案例研究中的贡献仍然未知。