硫酸生产废水中砷去除方法的研究

对硫酸生产中水洗净化工序排放的废水分别采用灰灰石和鼓风氧化法,铁屑法和铁盐法进行处理试验,结果表明,采用铁盐法级处理工艺处理废废水是可行的,控制组处理的ＰＨ分别为８－１０和８－９,Ｆｅ／Ａｓ摩尔比分别为１和５,当进水Ａｓ含量为１１５ｍｇ／Ｌ时,经两组处理后,出水Ａｓ含量〈０．５ｍｇ／Ｌ,重金属离子,ＰＨ,ＳＳ等指标均符合国家排放标准。     

风化煤吸附镉的动力学特性研究

风化煤具有不同孔径和较大的比表面积,又含有大量腐殖酸,其羧基、羟基等活性含氧官能团具有离子交换和络合能力,对各种含重金属离子废水有良好的净化效果.加之风化煤资源丰富、价格低廉,因而是一种很有希望的吸附剂.我们对风化煤吸附镉的动力学特征及影响吸附净化的因素进行了初步探讨.     

污水处理场运行的改进与优化

从荆门石化污水处理场的改扩建入手，分析了投用后存在的主要问题，针对隔油、浮选、生化各单元的运行进行了改进与优化     

酸溶-微波热解法从粉煤灰中制取聚合氧化铝的研究

从粉煤灰中提取聚合氧化铝（ＰＡＣ）是粉煤灰综合利用的途径之一。本研究提出了酸溶 微波热解从粉煤灰中制取ＰＡＣ的方法。通过工艺原理分析和试验，阐述了该工艺的可行性和合理性     

浑河沈阳段国控监测点位认证的技术方法

本文采用综合技术法辅以历史数据估算法对浑河沈阳段监测断面进行认证．根据监测数据筛选出５种主要污染指标后，按监测断面历史沿革分３个阶段分别用不同的统计方法对监测数据进行综合分析．用该法论证的结果，浑河沈阳段设置的３个断面，具有科学性合理性和可行性．     

Description of adsorption of hydrophobic organic compounds on sediment using multi-component adsorption model

ＩｎｔｒｏｄｕｃｔｉｏｎＴｈｅｔｒａｎｓｐｏｒｔａｎｄｆａｔｅｏｆＨＯＣｓｉｎｔｈｅｅｎｖｉｒｏｎｍｅｎｔｉｓｈｉｇｈｌｙｄｅｐｅｎｄｅｎｔｕｐｏｎｔｈｅｉｒｓｏｒｐｔｉｖｅｂｅｈａｖｉｏｒｏｎｓｏｉｌａｎｄｓｅｄｉｍｅｎｔ.ＭａｎｙｓｔｕｄｉｅｓｈａｖｅｂｅｅｎｒｅｐｏｒｔｅｄｔｈａｔｔｈｅｐｒｅｄｏｍｉｎａｎｔｓｏｒｂｅｎｔｏｆＨＯＣｓｉｎｓｏｉｌ ｓｅｄｉｍｅｎｔｉｓｎｏｒｍａｌｌｙｔｈｅｓｏｉｌ ｓｅｄｉｍｅｎｔｏｒｇａｎｉｃｍａｔｔｅｒ (ＳＯＭ)ｆｒａｃｔｉｏｎ ,ａｎｄｔｈｅｓｏｒｐｔｉｏ…     

运城市乡村企业发展中的若干环境问题及控制对策

快速、蓬勃发展的乡村企业对繁荣乡村经济,改变乡村产业结构,促进与增加农村居民收入及提高农村居民生活质量发挥着十分重要的作用.但是,由于缺乏正确的引导和规划,许多已经发展起来的乡村企业在创造社会财富,促进农村经济发展的同时,对当地自然生态环境带来了很大的压力并且严重影响和制约着当地居民的生活质量与乡村企业及乡村经济的进一步发展与壮大.本文通过运城市乡村企业的污染调查,论述了运城市发展乡村企业所带来的环境污染与危害,分析了乡村企业污染产生的主要原因与症结,提出了加强和改进乡村企业环境污染控制的对策与措施,喻示了乡村企业与自然生态环境相协调共发展之必然.     

连云港地区地震灾害背景分析

本文从震灾史料中发掘出连云港地区震灾的严重性，进而论述了连云港地区成灾背景，并对该地区震害分布及特点进行分析，可为有关部门制定防震减灾对策提供参考.     

离子色谱法测定酸沉降样品中的阳离子

用新型的阳离子分离柱和抑制柱分析雨水中的阳离子（Ｎａ＾＋、ＮＨ４＾＋、Ｋ＾＋、Ｍｇ＾２＋、Ｃａ＾２＋）对这种方法的准确性和可行性进行了论证。     

Dynamics of microcystins-LR and -RR in the phytoplanktivorous silver carp in a sub-chronic toxicity experiment

A sub-chronic toxicity experiment was conducted to examine tissue distribution and depuration of two microcystins (microcystin-LR and microcystin -RR) in the phytoplanktivorous filter-feeding silver carp during a course of 80 days. Two large tanks (A, B) were used, and in Tank A, the fish were fed naturally with fresh Microcystis viridis cells (collected from a eutrophic pond) throughout the experiment, while in Tank B, the food of the fish were M. viridis cells for the first 40 days and then changed to artificial carp feed. High Performance Liquid Chromatography (HPLC) was used to measure MC-LR and MC-RR in the M. viridis cells, the seston, and the intestine, blood, liver and muscle tissue of silver carp at an interval of 20 days. MC-RR and MC-LR in the collected Microcystis cells varied between 268-580 and 110-292 microg g(-1) DW, respectively. In Tank A, MC-RR and MC-LR varied between 41.5-99.5 and 6.9-15.8 microg g(-1) DW in the seston, respectively. The maximum MC-RR in the blood, liver and muscle of the fish was 49.7, 17.8 and 1.77 microg g(-1) DW, respectively. No MC-LR was detectable in the muscle and blood samples of the silver carp in spite of the abundant presence of this toxin in the intestines (for the liver, there was only one case when a relatively minor quantity was detected). These findings contrast with previous experimental results on rainbow trout. Perhaps silver carp has a mechanism to degrade MC-LR actively and to inhibit MC-LR transportation across the intestines. The depuration of MC-RR concentrations occurred slowly than uptakes in blood, liver and muscle, and the depuration rate was in the order of blood>liver>muscle. The grazing ability of silver carp on toxic cyanobacteria suggests an applicability of using phytoplanktivorous fish to counteract cyanotoxin contamination in eutrophic waters.