Size-fractionation and characterization of landfill leachate and the improvement of Cu2+ adsorption capacity in soil and aged refuse

Leachate was collected from an anaerobic lagoon at Shanghai Laogang refuse landfill, the largest landfill in China, and the sample was separated into six fractions using micro-filtration membranes, followed by ultra-filtration membranes. Several parameters of the samples were measured, including chemical oxygen demand (COD), total organic carbon (TOC), total solids (TS), pH, total phosphate (TP), total nitrogen (TN), fixed solids (FS), NH4+, orthophosphate, color, turbidity, and conductivity. These parameters were then quantitatively correlated with the molecular weight cutoff of the membrane used. Organic matter in the dissolved fraction (MW<1kDa) predominated in the leachate, accounting for 65% of TOC. Thermal infrared spectroscopy was used to characterize the filter residues. Asymmetric and symmetric stretching of methyl and methylene groups, and of functional groups containing nitrogen and oxygen atoms, were observed. In addition, the ability of two different samples to adsorb heavy metals was tested. Cu2+ was chosen as the representative heavy metal in this study, and the samples were soil; aged refuse, which had spent 8 years in a conventional sanitary landfill; and samples of soil and aged refuse treated for 48h with leachate in the ratio of 5g of sample per 50ml of leachate. Cu2+ uptake by the raw soil was approximately 4.60microg/g, while uptake by the leachate-contacted soil and leachate-contacted aged refuse were 5.66 and 5.11microg/g, respectively. These results show that the organic matter in the leachate enhanced the capacity of aqueous solutions to adsorb Cu2+.     

农业非点源污染环境影响及防治

非点源污染也称面源污染,因其污染的时空范围广,不确定性大,污染严重,对其治理及管理的难度也较大.由于化肥和农药的大量使用,农业非点源已成为中国水环境的主要污染源.文章中对农业非点源污染的特点、来源和危害进行了系统论述,并提出防治农业非点源污染的具体措施建议.     

Effects of UV-modified biochar derived from phytoremediation residue on Cd bioavailability and uptake in Coriandrum sativum L. in a Cd-contaminated soil

Environmental Science and Pollution Research - Biochar has been applied widely as an amendment in the remediation of contaminated soil to immobilize the heavy metals. However, the role of...     

碳源及反硝化芽孢杆菌强化低C/N比景观水体的生物脱氮

实验探讨了添加碳源及投加反硝化细菌对低碳氮比景观水体生物脱氮的影响。结果表明,有机碳源及B.subtilis FS05均能显著促进实验水体的生物脱氮作用,实验水体在28℃静置72 h后,乙醇添加组的TN、氨氮、硝酸盐及亚硝酸盐的去除率分别达到了62.7%、67.0%、69.8%和29.4%,而同样条件下,B.subtilis FS05投加组的去除率分别达到了66.9%、73.4%、66.0%和82.2%。从水质变化趋势可以看出,投加B.subtilis FS05能在更短时间内完成生物脱氮过程,其中,硝酸盐和亚硝酸盐去除速率最快,分别仅需要18 h和12 h。     

上海市大气PM2.5中溶剂可抽提有机物的特征研究

利用溶剂抽提、分离、毛细管气相色谱-质谱联用技术对2000年10月至2001年8月上海市5个不同功能区采集的大气PM_(2.5)样品中的溶剂可抽提有机物进行了检测,共检测出正构烷烃、单环芳烃、多环芳烃、有机酸、有机醇、有机酯等各类溶剂可抽提有机化合物267种。检出的82种多环芳烃中有15种属于美国EPA优先控制污染物名单。比较了不同季节、不同区域PM_(2.5)样品中正构烷烃、多环芳烃等化合物分布特征的差异。检出的喹啉类含氮杂环类化合物以及有机酸等污染物表现出一定的机动车排放特征。     

跨海大桥主墩桩基钢护筒腐蚀损伤识别

跨海大桥主墩桩基施工过程中采用的钢护筒被保留作为桩基的外层,容易受到海洋环境的腐蚀破坏。提出一种基于插值曲率模态指纹库比对的桩基损伤识别方法,为解决测试数据不完备的问题,采用三次样条函数几何插值得到扩展后的桩基振型,然后在扩展振型的基础上采用中心差分计算得到曲率模态指标。以金塘大桥为工程背景,建立索塔-基础多尺度有限元模型,考虑海水腐蚀造成桩基钢护筒局部损失情况,以损失减薄区域的位置、轴向长度、深度为损伤参数,设置多种损伤工况样本,计算并建立基于插值曲率模态的桩基损伤识别指纹库,最后通过指纹库以外损伤工况与库内样本比对的方式,验证损伤识别效果。研究表明,为保证三次样条函数几何插值得到扩展振型对真实振型的拟合精度,至少需要沿桩基均布6个位移插值点。通过指纹库比对,能够准确识别桩基钢护筒减薄区域的位置与轴向长度。     

中国自然资源学会2005年学术年会在济南召开

2005年11月14日,中国自然资源学会2005年学术年会在山东师范大学隆重召开。大会历时两天,来自全国84个科研院所和大专院校的280名代表参加了会议。本次大会的主题是“发展资源科技,建设节约型社会”。围绕该主题,设立了4个专题,即:“节约型社会的资源科学理论与技术”、“资源持续利用、开发保护与节约型社会”、“土地资源节约利用与技术”、“湿地资源的保护、生态修复与区域可持续发展”。本届年会还首次设立了“资源学院院长论坛”,该论坛的设立是本次大会的创新点,目的在于促进我国资源学科建设,培育资源学科人才,加强各兄弟院校和科研单位的合作,推进资源科学的发展。     

非点源污染河流的水环境容量估算和分配

通过河流相应集水区内氮磷的各污染源分析(包括农地、畜禽养殖和生活排污等),利用输出系数模型估算各非点源的氮磷投(排)放量和入河量;采用河段氮磷输入-输出平衡关系分析方法,估算河流对氮磷的每月自净量.以此为基础,参照水功能区划所要求的水质目标,提出了水质未超标河段相应集水区的氮磷剩余水环境容量按月估算模型,和水质超标河段相应集水区内氮磷投放削减量的按月估算模型,及其在各污染源之间的分配方案.结果表明,长乐江的总氮和总磷自净量分别达到775.9 t·a^-1和30.9 t·a^-1,自净率分别为28.8%和51.2%.河流对氮磷的自净量不仅受水文生态条件的影响而表现出较大的季节性变化,而且随着污染负荷量本身的增加而提高.按照水功能区划中Ⅲ类水的水质要求,长乐江总氮含量全年超标;各非点源的总氮投(排)放量均须不同程度的削减,削减总量应达到1 581.0　t;氮源削减量分配结果表明,化肥是应削减的最大氮源,要求在河流相应集水区内的化肥氮投放削减量为1 047.4 t·a^-1;而与各种氮源的投排放现状相比,要求削减比例最高的是畜禽养殖的氮排放量,达32.4%.长乐江流域尚有一定的总磷剩余水环境容量(2 335.7 t·a^-1).根据目标水质要求,平水期是各污染源总氮投放需要削减的量最大的时期,丰水期则是总磷剩余水环境容量最小的时期.