以回收利甩标准破解“垃圾围城”

生活垃圾处理已经成为各城市面临的难题。在已有研究基础上分析了城市垃圾分类收集存在的严重问题和影响居民实施垃圾分类的关键因素,概述了现有的垃圾分类收集标准和废弃产品回收利用标准内容,最后提出加强实施相关标准、促进垃圾分类收集的建议。     

LS—931Al2O3基硫磺回收催化剂的工业应用

LS－931催化剂是新开发的Al2O3基硫磺回收催化剂，经洛阳炼油厂5000t/a装置使用考察结果证实其具有高活性和稳定性运行的特点。在第一转化器使用LS－931Al2O3基催化剂及在第二转化器仍然使用旧的LS－811Al2O3催化剂的情况下，与原来单纯使用LS－811Al2O3催化剂相对比，装置总硫转化率可提高1％左右，有机硫水解率达到96.4%，尾气中的硫化物含量则稳定地降至1％（V）以下。     

电渗析法处理造纸黑液回收碱的试验研究

进行了单阳膜电渗析法从造纸黑液中回收碱液试验，结果表明该法回收吨碱的电渗析电单耗可稳定在３０００ｋＷｈ左右，比氯碱厂生产烧碱和黑液燃烧法回收碱的能耗都低。当回收终点ｐＨ为７时，Ｎａ＾２＋回收率为５０％，阳极黑液含Ｎａ＾＋为５０００￣７０００ｍｇ／Ｌ，可直接回用于生产工段。而本试验所采用的钛涂镣电极使用耐久性欠佳，尚有待改进。但该法仍不失为处理造纸黑液的可选方案。     

老化石油污染土壤的清洗处理

以华北油田老化长达1年以上的石油污染土壤为研究对象,采用自行选配的清洗剂对该污染土壤进行了一次清洗和二次清洗处理.实验结果表明,一次清洗后,污染土壤样品的含油率从26.34%～29.90%降到6.34%～7.84%,洗油率达80.06%～81.06%;经二次清洗处理后,污染土壤样品的含油率从26.34%～29.90%降到4.05%～4.85%,洗油率达88.06%～88.19%.在一次清洗和二次清洗的基础上,通过模拟实验确定了洗油污水回用的最佳回用率为80%,最佳加药质量浓度为0.4 g/L,该条件下污水的最终产生量也较少.按照该参数对华北油田的石油污染土壤进行了清洗实验,洗油率达79.20%～80.51%.     

含铅废水处理技术及其展望

详细介绍了含铅废水的 5种主要处理方法 ,包括化学沉淀法、离子交换法、液膜法、生物吸附法及电解法 ,对各种方法的优缺点及发展现状进行了介绍 ,另外 ,还对含铅废水处理的前景进行了展望 ,提出了电解法与离子交换法或与生物吸附法相结合是处理含铅废水的发展方向。     

多环芳烃污染土壤生物修复的强化方法

生物降解是去除环境中多环芳烃(PAHs)的重要途径,通过采取一些强化措施,如使用表面活性剂,添加营养物质和提供共代谢底物等,可显著提高PAHs降解速度和程度,为生物修复技术的成功应用提供前提。在分析中,对近年来国内外在PAHs污染土壤生物修复强化方面的研究进展进行了综述。     

含铜蚀刻废液的回收与利用

某酸性蚀刻废液和碱性蚀刻废液混合得到沉淀物———Cu(OH)Cl,过滤后该沉淀物可与浓H2SO4反应生成CuSO4产品,而残留废水中的Cu2 可通过Na2S去除。实验室小试结果表明,当该酸性和碱性蚀刻废液以5∶13的体积比混合时,可以使Cu(OH)Cl得到最大限度的沉淀(96.53%的铜沉淀);当以15∶4的质量比(Na2S∶Cu2 )投加Na2S时,残留废水中的Cu2 可以最大限度的去除(98.78%的铜离子得到去除)。此后的工程实践对具体的工艺操作进行了调试,验证了此工艺回收与利用含铜蚀刻废液的可行性。     

Temporal Trends in Water Chemistry in the Turkey Lakes Watershed Ontario,Canada, 1982-1999

The Turkey Lakes Watershed (TLW) was established in 1980 as asite for study of the ecosystem effects of acidic deposition, andsince then there has been 40% reduction in North AmericanSO₂ emissions. Monitoring records for bulk deposition,shallow and deep ground water, two headwater streams and two lakeoutflows have been tested to identify statistically significantmonotonic trends. The TLW appears to be responding to decliningacidifying emissions because the most prevalent chemical trendacross sample types/stations was decreasing SO₄ ^2-. Increasing pH was detected in four of the seven data sets, butonly the H⁺ decrease in bulk deposition was of a magnitudeto be an important ionic compensation for the SO₄ ^2-decline. There is little evidence of acidification recovery inTLW waters however. Increasing alkalinity was found only in theoutflow of the penultimate lake of the basin, and in fact, deepground water and the other lake outflow had decreasing alkalinitytrends (i.e., continuing acidification). For the surface waterstations, the greater part of the ionic compensation fordeclining SO₄ ^2- was decreasing base cations, and as aresult, these waters are probably becoming more dilute with time,although only the headwater streams exhibited decliningconductivity. Five of seven data sets had increasing dissolvedorganic carbon concentrations. Increasing NO₃ ^- wasimportant in ground waters. Drought has strongly influencedtrends and delayed recovery by mobilizing S stored in catchmentwetlands and/or soils.     

从银铅锌废渣中回收硝酸银的研究

介绍了用灼烧、浸取、沉淀、溶转和离子交换等方法,从银铅锌废渣中直接回收硝酸银,收率可达80.12%,AgNO3纯度为99.9%。考察了试料粒度、FeCl3质量浓度、溶液酸度、固液比,反应温度及浸取时间对银浸出率的影响。     

Recovery of Acidified Lakes: Lessons From Sudbury, Ontario, Canada

Over 7,000 lakes around Sudbury, Ontario, Canada were acidified by S deposition associated with emissions from the Sudbury metal smelters and more distant S sources. Air pollution controls have led to widespread changes in damaged Sudbury lakes, including increased pH and decreased concentrations of SO₄, metals and base cations. While chemical improvements have often been substantial, many lakes are still acidified, although water quality recovery is continuing. Biological recovery has been observed in some lakes among various groups of organisms including fish, zooplankton, phytoplankton and zoobenthos. Generally, however, biological recovery is still at an early stage. Lakes around Sudbury are also showing that the recovery of acid-damaged lakes is closely linked to the effects of other major environmental stressors such as climate change, base cation depletion and UV-B irradiance. Future studies of the recovery of acid-damaged lakes around Sudbury, and in other regions, will need to consider the interactions of these and other stressors.