太湖流域典型区域纺织行业污染特征分析

基于2009年太湖流域各市污染源统计及调查数据,分析了近年太湖流域典型区域的纺织行业空间分布特征和污染特征,利用经济贡献率、污染贡献率2项指标识别了重污染行业,利用污染物排放不公平系数、资源消耗不公平系数指标评价了不同规模企业的经济发展与污染排放及资源消耗的协调关系.结果表明,研究区内66.1％的纺织企业分布于武进区、惠山区和宜兴市.棉、化纤印染精加工业是该区域纺织行业的主导产业,企业数量占56％,经济贡献率为72.8％,工业废水、COD及氨氮等污染物贡献率分别高达88.7％,81.5％和89.1％.棉、化纤印染工业总产值小于5千万的纺织企业数量占81.6％,经济贡献率仅为0.73％,且经济贡献与污染、资源消耗贡献匹配性差,污染排放和资源消耗的不均衡性尤为突出.     

人工湿地处理农村生活污水应用研究

近年来,随着新农村建设广泛开展,加快推进农村生活污水治理迫在眉睫。人工湿地处理农村生活污水是一种相对低碳、绿色的生态处理模式,倍受关注。本文阐述了人工湿地处理污水的作用机理,归纳分析对比了几种复合型人工湿地处理工艺在农村生活污水处理中的应用,最后提出复合人工湿地工艺处理农村生活污水的选用原则。     

污泥焚烧中二氧化硫检测新方法及污泥处理探讨

对新乡市9个污水处理场污泥预处理后,用测硫仪分析污泥含硫量,并用经验公式根据年污水处理量,估算焚烧污泥方法年二氧化硫排放总量。结果显示：用测硫仪测定污泥含硫量,核算二氧化硫排放量,与现有方法相比,操作简便易行,结果不受采样条件、时间、环境、布点等因素影响,重现性好、完整、精密。同时发现部分污泥含硫量超过规定用煤中含硫量,建议用焚烧方法处置污泥,净化尾气。     

关于内蒙古河套灌区面源污染防治的几点建议

河套灌区的主体为后套平原,总土地面积为1万平方公里,主要为黄河冲积平原。由于化肥、农药的大量使用,致使河套地区地表水体和地下水氮、磷普遍超标。本文针对河套面源污染问题,提出了几点防治措施。     

基于BP人工神经网络的长江口外海生态综合评价及其成因分析

以长江口外海域为研究区域,基于2008年秋季该海域2个峰面断面的海洋环境调查走航数据,以海水水质指标、浮游植物多样性指数及叶绿素a浓度为评价指标,运用BP人工神经网络的方法评价该海域生态环境质量状况,结合该海区的地形及水动力情况分析,结果表明:2008年秋季长江口外海域生态状况总体处于亚健康状态;31°N断面受长江冲淡水影响,生态状况近海劣于远海,但20号站位逆趋势好转,据监测,夏季其附近海域为赤潮高发区;30°N断面近岸受浙江沿岸上升流影响,生态状况好于31°N,但5号站位逆趋势恶化;5号和20号站位反映了上升流与长江口冲淡水的交汇区域的生态状况。BP人工神经网络用于生态环境评价,具有一定的客观性和通用性。     

基于ASP.NET的安全信息管理系统

安全信息管理系统主要包括对安全信息数据的收集、存储、加工处理、传递和利用等功能.本文主要阐述了B/S结构的特点,以及一种全新的Web开发技术ASP.NET在安全信息管理系统中的应用.这使在Web上对安全信息数据进行增、删、改、查操作成为可能,对防止事故发生,减少由事故造成的损失,提高企业的安全管理水平等具有重要的现实意义.     

水产品中甲氰菊酯残留的ELISA快速检测

为快速检测水产品中甲氰菊酯的残留,应用水溶性碳化二亚胺(EDC)法将甲氰菊酸与牛血清白蛋白(BSA)和卵清蛋白(OVA)偶联,合成了甲氰菊酯的人工免疫抗原和包被抗原.免疫抗原经紫外扫描和聚丙烯酰胺电泳验证构建成功,用此抗原免疫试验兔子,获得了甲氰菊酯的多克隆抗体.经检测,抗体对甲氰菊酯具有较好的特异性和灵敏性.在此基础上建立了水产品中甲氰菊酯残留的间接ELISA检测法.理想的甲氰菊酯-OVA包被抗原质量浓度为1.6 mg/L,酶标二抗(羊抗兔IgG-HRP)的稀释度为1∶1000,多抗的稀释度为1∶3 200,最适检测范围为20～200 μg/kg,在实际样品检测时的最低检出限为20 μg/kg,接近或达到气相色谱法的测定水平,但检测速度大大提高,可在3 h内完成近百个样品的分析,适合甲氰菊酯的快速检测.     

土壤中多环芳烃的SPMD辅助解吸行为研究

为了开发一种表征土壤中憎水性有机污染物解吸及生物有效性的新方法,建立了半透膜被动采样装置（SPMD）研究土壤中有机污染物解吸行为的方法,利用SPMD分析了多环芳烃菲、芘和苯并［a］芘在3种不同性质土壤中的辅助解吸行为.结果表明,SPMD是一种很好地表征土壤中憎水性有机污染物解吸及生物有效性的手段. SPMD辅助解吸多环芳烃的效率与土壤有机质及多环芳烃性质有关.随着土壤有机质含量的降低,土壤中菲和芘的SPMD解吸率逐渐升高,对于10 mg/kg染毒水平,当土壤有机质含量由18.68%降低到0.3%时,2种化合物的解吸率分别由56.45%和48.28%上升到接近100%;但是对于苯并［a］芘,粘土表现出明显的滞留能力,在有机质含量（0.3%）很低、粘土含量（39.05%）较高的3号土壤中,苯并［a］芘的解吸率仅有66.97%.不同多环芳烃SPMD辅助解吸率差别很大,随着土壤有机质含量的降低,以及污染物浓度的提高,菲和芘的解吸差异逐渐缩小,而苯并［a］芘与上述2种多环芳烃的差异很大,主要是由于苯并［a］芘具有高度亲脂性,并且分子较大,造成其容易滞留在粘土的微孔及有机质的致密结构中.     

Kinetics of enzymatic unhairing by protease in leather industry

In leather industry, unhairing is a heavy pollution operation. The conventional lime-sulfide process produces a large amount of sulfide which is toxic to health and difficult to dispose. Moreover, conventional lime-sulfide process leads to the destruction of the hair causing increased COD, BOD and TDS loads in the effluent. As an alternative method, enzymatic unhairing is a promising clean technology. The main utilized enzyme preparations are proteases.There are many reports about enzymatic unhairing, most of which are qualitative. The kinetics of enzymatic unhairing by protease was discussed in this article. It will provide useful information to enzymatic unhairing. In our research, by analysis of the concentrations of released total protein in enzyme bath during protease unhairing, the good linearity between released total protein and square root of time (min^1/2) was obtained at the initial stage. The good linearity suggests that enzymatic unhairing by protease is a diffusion-controlled process at the initial stage. The analysis of kinetics of released saccharides also confirms the same conclusion. On the other hand, the same characteristics between the kinetics of released saccharides and that of released total protein further confirms that it is the hydrolysis of core protein by protease that leads to the degradation of proteoglycans and the release of protein and saccharides. However, in our tests, the kinetics of released collagen indicates that the injury to skin took place in 3-6 h. Therefore, it’s necessary to control the time of protease unhairing within an appropriate limit.     

Mobilities and leachabilities of heavy metals in sludge with humus soil

Chemical forms of Zn, Ni, Cu, and Pb in municipal sewage sludge were investigated by adding humus soil to sludge and by performing sequential extraction procedures. In the final sludge mixtures, Zn and Ni were mainly found in Fe/Mn oxide-bound (F3) and organic matter/sulfide-bound (F4) forms. For Zn, exchangeable (F1), carbonate-bound (F2), and F3 forms were transformed to F4 and residual forms (F5). For Ni, F1 and F2 forms were transformed to F1, F2, and F3 forms. Both Cu and Pb were strongly associated with the stable forms F4 and F5. For Cu, F2 and F3 forms were major contributors, while for Pb, F3 and F4 forms were major contributors to F5. Humus soil dosage and pH conditions in the sludge were strongly correlated with the forms of heavy metals. Five forms were used to evaluate metal mobilities in the initial and final sludge mixtures. The mobilities of the four heavy metals studied decreased after 28 days. The metal mobilities in the final sludge mixtures were ranked in the following order: Ni > Zn > Cu = Pb. Leaching tests showed that the mobilities of Zn and Ni in lower pH conditions (pH 4) were higher than those in higher pH conditions (pH 8).