小麦麸皮水浸提液对铜绿微囊藻(Microcystis aeruginosa)光合色素含量和叶绿素荧光诱导动力学的影响

小麦麸皮水浸提液(WBL)对铜绿微囊藻(Microcystis aeruginosa)具有较强的抑制作用.为了阐明铜绿微囊藻光合系统对WBL胁迫的响应,本文分析了WBL胁迫下M.aeruginosa CHAB-109细胞光合色素含量及叶绿素荧光诱导动力学变化.结果显示,当WBL浓度为1.6和3.2 g/L时,M.aeruginosa CHAB-109单位细胞内Chl.a和类胡萝卜素含量均显著低于对照.Chl.a光诱导荧光动力学分析结果显示,WBL胁迫下单位反应中心吸收的光能(ABS/RC)、单位反应中心捕获的用于还原QA的能量(TR0/RC)及单位反应中心捕获的用于电子传递的能量(ET0/RC)均受到显著抑制.光合系统Ⅱ(PSⅡ)能量分配比率参数分析结果显示,WBL对光合系统反应中心电子供体侧没有影响,但是显著抑制光合系统反应中心电子受体侧电子传递.综合分析WBL诱导下M.aeruginosa CHAB-109 PSⅡ能量流动比活性能参数和能量分配比率参数显示,反应中心电子受体侧电子由反应中心传递到QA及QA更远的部位均为WBL的抑制作用位点.     

Application of geophysical monitoring techniques as aids to probabilistic risk-based management of landfill sites

Increasingly stringent regulatory regimes, in conjunction with landfill development in environmentally sensitive locations and the large number of abandoned landfill sites, are significantly increasing the responsibilities of local authorities and environmental agencies. These responsibilities include the identification and/or monitoring of: locations of contaminated land; boundaries of waste sites; nature of the landfill content; location, extent, content and depth of closed landfill sites; leachate plumes escaping from both operational and closed sites and the performance of landfill liners. Probabilistic risk based modelling is a standard methodology for monitoring and managing the environmental impact of landfill sites. A critical problem in the implementation of probabilistic risk based modelling is the large uncertainty in the shallow geology, internal structure and leachate distribution of landfills caused by the severe lack of both surface and subsurface information from within and outside the landfill site. The utility of two non-invasive ground based geophysical monitoring techniques, ground penetrating radar and reflectance spectroscopy, as aids to characterising the three-dimensional structure and distribution of leachate within a landfill has been investigated. Strong correlations between red edge inflection position and chlorophyll and metal concentration have been demonstrated from grassland species affected by leachate contamination of the soil adjacent to the landfill study site. The results of this study have demonstrated how recent advances in equipment, techniques and software mean that field-based reflectance spectroscopy and Ground Penetrating Radar can now provide environmental scientists with cost-effective, rapid techniques to characterise landfill sites in three dimensions, aid landfill managers in positioning additional boreholes and field sampling surveys, and provide data as inputs to leachate migration modelling.     

钻孔灌注桩施工过程中垃圾渗滤液对地下水的污染分析

采用大直径钻孔灌注桩时,施工时会破坏现有垃圾填埋场的防渗体系,且渗滤液将对地下水造成一定程度的污染。通过对基桩施工过程中渗滤液污染传输过程以及特征进行分析,提出了包括全护筒支护、膨润土泥浆护壁以及减少钻孔成孔至灌注混凝土的间隔时间等控制污染的主要措施,建立了基桩施工过程中钻孔泥浆浆液的损失模型以及渗滤液传输到地水下中的污染物质浓度的计算模型。根据某一具体施工条件进行估算,预测了地下水中污染物质浓度以及污染程度。最后,提出了垃圾填埋场内钻孔灌注桩的施工工艺以及施工注意事项。     

中水灌溉下重金属在土壤中的垂直迁移及其对地下水的污染风险

中水灌溉是解决水资源短缺的潜在途径,关于中水灌溉条件下土壤中重金属的迁移行为及其对浅层地下水的污染风险至今仍缺乏研究。本文通过土柱模拟试验,分析中水灌溉条件下重金属在土壤中的迁移趋势及其对浅层地下水的污染风险。试验用添加重金属（As、Cd、Cu、Pb浓度分别为2、0.2、20、20 mg.kg-1）的人工污水和中水以1年、3年的灌溉量进行土柱淋溶实验。结果表明,淋溶20天（1年的灌溉量）以及60天（3年的灌溉量）,灌溉水中的As、Cd、Cu和Pb主要在表层（0¹0cm）累积。随着淋溶时间的延长,4种重金属（尤其是Cd）表现出向下迁移的趋势。但与地下水I级水质标准（GB/T14848-93）相比,淋滤液中4种重金属均未超标。因此,从本文的模拟试验来看,以北京市当前的中水进行灌溉,As、Cu、Pb对浅层地下水的污染风险不大。     

Metal speciation and attenuation in stream waters and sediments contaminated by landfill leachate

The degree of metal contamination (Zn, Pb, Cu, Ni, Cd) has been investigated in the vicinity of an old unmonitored municipal landfill in Prague, Czech Republic, where the leachate is directly drained into a surface stream. The water chemistry was coupled with investigation of the stream sediment (aqua regia extract, sequential extraction, voltammetry of microparticles) and newly formed products (SEM/EDS, XRD). The MINTEQA2 speciation-solubility calculation showed that the metals (Zn, Pb, Cu, Ni) are mainly present as carbonate complexes in leachate-polluted surface waters. These waters were oversaturated with respect to Fe(III) oxyhydroxides, calcite (CaCO₃) and other carbonate phases. Three metal attenuation mechanisms were identified in leachate-polluted surface waters: (i) spontaneous precipitation of metal-bearing calcite exhibiting significant concentrations of trace elements (Fe, Mn, Mg, Sr, Ba, Pb, Zn, Ni); (ii) binding to Fe(III) oxyhydroxides (mainly goethite, FeOOH) (Pb, Zn, Cu, Ni); and (iii) preferential bonding to sediment organic matter (Cu). These processes act as the key scavenging mechanisms and significantly decrease the metal concentrations in leachate-polluted water within 200 m from the direct leachate outflow into the stream. Under the near-neutral conditions governing the sediment/water interface in the landfill environment, metals are strongly bound in the stream sediment and remain relatively immobile.     

褐铁矿和白云石对垃圾渗滤液厌氧消化增强作用的初步研究

垃圾渗滤液治理一直是城市生活垃圾卫生填埋场的难题。能否利用矿物-微生物交互作用提高垃圾渗滤液有机污染物厌氧转化的效率是值得研究的问题。本文设置4组厌氧生物反应器(分别为只添加褐铁矿或者白云石、同时添加褐铁矿和白云石以及不添加矿物的空白组),考察添加褐铁矿、白云石对垃圾渗滤液厌氧消化的影响。实验结果表明,厌氧生化反应12 d时,添加了褐铁矿和白云石的反应器中COD去除率均达到80%以上,而空白对照组COD去除率仅为50%;4组反应器中溶液pH值变化表明,矿物的存在提高了溶液的pH值0.5左右;4组反应器中氨氮含量变化不大,也没有表现出明显差异。研究认为褐铁矿或白云石矿物在垃圾渗滤液中有机物的厌氧消化过程中起到了重要促进作用。研究结果为提高垃圾渗滤液厌氧处理效率提供了一个可供参考的方法。     

垃圾渗滤液的特征污染组分在包气带中的迁移转化规律

通过室内土柱实验,研究了垃圾渗滤液的特征污染组分氮、COD在包气带不同介质中的迁移转化特征。实验结果表明,岩性不同的包气带介质是影响氮素、COD迁移转化的重要因素之一,不同介质对氮、COD的净化能力不同;渗滤液对地下水不会造成氮素污染,但会造成有机污染。     

Redox Processes in Groundwater Impacted by Landfill Leachate

Groundwater downgradient from Trandum municipallandfill was investigated in summer 1996, with a viewto assessing the distribution of redox-sensitivespecies. The water table at Trandum is 10–26 metersbelow the surface. Monitoring well filters have beeninstalled at depths of up to 15 m below water table,covering an area of 400 m by 200 m. Groundwaterinfluenced by the landfill seems to be confined tothis area. Pristine groundwater has a chemicalsignature indicative of calcite and pyrite weathering.Groundwater influenced by leachate from the landfillexhibits an excess of alkalinity relative to calcium,which is likely to be derived from degradation oforganic matter in the landfill. Groundwaterimmediately below and downstream of the landfillcontains elevated concentrations of Fe and Mn, largelymobilized under reducing conditions from the aquifermatrix and reflected in depleted HNO₃-extractable Feand Mn in sediment samples from the same area.Groundwater samples allow the tentative identificationof redox zones based on oxidized and reduced forms ofFe, Mn, N and S. A methanogenic zone is notobserved.