废铅蓄电池回收铅与开发黄丹、红丹以及净化铅蒸汽新工艺研究

简述了废铅蓄电池回收铅的现状和不足,提出了废铅蓄电池再生铅与开发黄丹或红丹以及铅尘、铅蒸汽净化新工艺,经小试和小批量生产考核了工艺流程、优化了技术参数.     

微波诱导水解法制备纳米TiO_2及光催化降解盐酸四环素

采用微波诱导水解法快速制备了纳米TiO_2光催化剂,通过XRD、TEM、SEM、BET和EDS技术对其进行了表征。该方法可在10 min内制备出平均粒径约7.5 nm的锐钛矿相纳米TiO_2。采用该催化剂(加入量0.5 g/L)对盐酸四环素(TC,100 mg/L)进行紫外光催化降解,40 min时降解率高达92.9%,60 min时TOC去除率为81.7%,明显优于市售P25纳米TiO_2。这主要归功于所制备纳米TiO_2表面残留的有机物提高了光生电子-空穴对的分离能力,以及纳米粒子的小尺寸效应和较大的比表面积。溶液p H为9时TC的降解率更高。该催化剂具有较好的光催化稳定性。活性基团捕获实验表明,纳米TiO_2光催化降解TC过程中空穴起主要作用。     

高铁酸盐多功能水处理剂的制备及除污染技术

该发明涉及一种多功能水处理剂的制备与除污染技术。采用廉价的亚铁盐，经过改性处理得到反应活性较高的三价铁，再经过氧化过程制备高铁酸盐。本法工艺简单，能耗低，产品质量稳定，成本低廉。采用该发明制备的高铁酸盐产品，由于具有强氧化性并同时具有絮凝剂的特点，对天然水体中的多种污染物有广谱的去除作用。高铁酸盐预氧化处理具有氧化、吸附、共沉淀、消毒、杀菌、除藻等多功能的净水效能。     

专利文摘

降解多/杂环芳烃的仿酶型水处理剂及其制备方法该发明涉及一种降解多/杂环芳烃的仿酶型水处理剂及其制备方法。其技术方案是:将膨润土与去离子水按质量比1:(30～60)混匀,静置,取中间层,得纯化膨润土;再将纯化膨润土与NaCl     

利用铝型材厂污泥制备钛酸铝-莫来石复相材料的原料配方与方法

该发明提供了一种利用铝型材厂污泥制备钛酸铝-莫来石复相材料的原料配方与方法。其特征是：以铝型材厂污泥、高岭土和TiO2为原料，将原料混合，压制成型，经高温反应后制备成钛酸铝-莫来石复相材料。该发明属于固体废弃物的综合利用，不仅原料易得，制备方法简单，有利于废物利用，而且制备的材料为具有高附加值和无污染的优质耐火材料；     

多金属氧酸盐非均相光催化降解处理有机废水的研究进展

非均相光催化氧化是一种催化剂易于回收利用且研究广泛的高级氧化技术。本文综述了多金属氧酸盐(POMs)非均相光催化降解废水中有机污染物的研究现状。该类非均相光催化剂主要包括负载型POMs(载体主要有半导体氧化物、离子交换树脂和分子筛)、POMs复合膜材料、不溶性盐和多元复合物。讨论了其制备方法、降解效果、反应机理和重复使用性。最后,指出了该领域未来可能的研究方向,为该领域的进一步研究提供参考。     

负载型纳米TiO2光催化剂的制备及其光催化活性

采用悬浮聚合法制备粉煤灰-聚苯乙烯微珠载体,通过矿化接枝技术将水热法制备的纳米TiO2负载在粉煤灰-聚苯乙烯微珠载体上,制成负载型纳米TiO2光催化剂。用x射线衍射仪、扫描电子显微镜对负载型纳米TiO2光催化剂进行了表征;通过光催化降解甲醛实验评价了负载型纳米TiO2光催化剂的活性。实验结果表明,纳米TiO2在载体上分散良好,平均粒径为36．4nm;该催化剂活性较高,明显优于粉体纳米TiO2光催化剂,重复使用10次左右,该催化剂的活性无明显下降。     

用甲基硫酸钠废渣制备二甲基硫醚

根据酯在碱性条件下水解反应生成醚的原理，研究了以甲基硫酸钠废渣为原料制备二甲基硫醚（DMS）的方法。在反应温度100℃、加水量100mL、搅拌时间30min、合成反应时间50min的最佳工艺条件下，制得的DMS产品纯度为99％，收率为83．59％。该法工艺简单，技术可行，操作稳定，既消除了环境污染，又能制备化工产品，具有明显的环境效益和经济效益。     

专利文摘

一种用于光降解全氟有机酸的掺杂二氧化钛炭铁复合材料的制备方法该专利涉及一种用于光降解全氟有机酸的掺杂二氧化钛炭铁复合材料的制备方法。该掺杂二氧化钛炭铁复合材料是将纳米二氧化钛和纳米羟基铁固定在颗粒活性炭上,然后将该材料加入到全氟有     

生物细胞载体的制备方法

该专利公开了一种生物细胞载体的制备方法。其制备工艺为：(1)制备生物细胞载体专用树脂；(2)制备生物细胞载体的中空纤维；(3)生物细胞载体致孔剂处理。该发明具有制备工艺简单，操作方便，生物细胞载体比重小、柔软、耐生物腐蚀和纤维壁微孔分布均匀，纵横交叉密度大等优点，适用于培养生物细胞的生长载体、废水处理工程的微生物生长载体、水净化工程的反渗透膜和蓄电池的隔离膜等。／CN1556207，2004—12—22     

再生铅冶炼行业典型工艺的铅污染物质流分析

将物质流分析应用于我国再生铅冶炼行业典型工艺(铅膏炼前预脱硫—还原熔炼—精炼)的铅污染研究,构建了再生铅冶炼过程的铅元素流图,并针对铅污染提出了应对措施。研究结果表明:再生铅典型工艺的铅直收率、铅回收率、铅废物循环利用率分别为85.38%,93.96%,97.57%;应重点监控的铅有组织排放依次为外排烟气、熔炼渣、脱硫石膏渣;针对外排烟气中铅烟尘的PM2.5占比高及铅烟尘活性较高易于释放的特点,应选用高效除尘器,进一步提高细烟尘的捕集率;铅无名损失的重点工序依次为熔炼工序、电解精炼工序、合金熔铸工序;冶炼烟尘返回熔炼炉时,应增加制粒工序,以降低熔炼炉的烟尘率。     

黑白显像管玻壳铅尘中铅的提取方法

研究了黑白显像玻壳生产中产生的含铅粉尘的水溶性,酸溶性,浸出毒性和铅的存在形态,提出了用盐酸循环浸铅,冷析ＰｂＣｌ２的提铅方法,考察了浸取剂及浓度,浸取温度,浸取时间对铅浸出率的影响,为充分利用铅资源及实现铅尘无害化提供了依据。     

铅蓄电池行业清洁生产要点探讨

针对我国铅蓄电池行业现状,从铅蓄电池生产所用原辅材料、生产工艺装置、过程控制、末端治理、职业卫生、废电池回收、生产能力要求及布局等多个角度出发,对该行业开展清洁生产的各个要点环节进行了探讨研究。     

铅冶炼烟尘的物性分析及浸出性研究

采用XRF、XRD、激光粒度分析、DTA-TG、FTIR以及SEM-EDS等技术,对某铅冶炼厂烟尘（简称烟尘）进行了物性分析,并采用稀硫酸对烟尘进行了浸出性研究。分析结果表明：烟尘所含主要元素为Pb,Zn,Cd,Cl,S,As;烟尘是氧化物、硫酸盐、硅酸盐、硫化物和砷化物等物质的混合物,主要物相为ZnO,PbO,PbSO₄,CdO,CdS;烟尘颗粒大小不一,形状各异,多呈相互黏结或包裹状。实验结果表明：在ρ（硫酸）=120 g/L、浸出时间30 min、液固比（稀硫酸体积（mL）与烟尘质量（g）之比）20∶1、浸出温度60 ℃的条件下,Pb,Zn,Cd,As,Cl的浸出率分别达到0.16%,98.95%,49.36%,89.12%,99.31%。     

生物炭对铅离子的吸附性能

以废弃松木屑为原料,采用控制热分解法制备了生物炭。运用BET和FTIR等技术对生物炭进行了表征,考察了生物炭对铅离子的吸附效果,并探讨了吸附机理。表征结果显示,700℃氨气处理的生物炭,其比表面积和总孔体积显著增大。实验结果表明:生物炭对铅离子的吸附效果优于普通活性炭,且以700℃氨气处理的生物炭为最佳;随溶液pH的升高生物炭对铅离子的去除率增大,当pH为4~6时去除效果较好;在溶液pH为6、初始铅离子质量浓度为50 mg/L、吸附剂加入量为1 g/L、吸附时间为6 h的条件下,700℃氨气处理的生物炭对铅离子的去除率达99%以上;700℃氨气处理的生物炭的Langmuir吸附常数和Freundlich吸附常数远大于普通活性炭和其他工艺的生物炭;铅离子在生物炭上的吸附过程符合拟二级动力学方程。     

我国大气铅浓度水平与污染源排放特征

总结和评价了我国大气铅浓度水平、大气铅污染源的主要类型和排放特征,对今后我国大气铅污染发展趋势进行了说明.汽油无铅化以后,我国城市大气环境中的铅浓度有所下降,一般不超过国家标准的限值,但农村地区大气铅污染状况应引起高度重视.涉铅工业排放、燃煤排放和汽车尾气是大气铅污染的主要来源.我国大气铅污染源涉及行业和部门庞杂,伴随着铅产品的整个生命周期.     

Urban Metal Management The Example of Lead

The metal metabolism of an urban region, the City ofVienna, was investigated to discuss urban metal management strategies in view of environmental protection and resource conservation. About 90% of the metal stock is located in Vienna's buildings and infrastructure, whilst only 10% is in the landfills. The city stock represents a potential source for diffusive emissions. However, the control of the current environmental policy concentrates mainly on landfill emissions. Diffusive emissions resulting from the losses over the use of metal containing goods in the city are widely dispersed and cannot be easily controlled due to numerous non-point sources. First investigations indicate that for certain applications, the diffusive stock emissions are as significant as other sources. At present, Vienna's known diffusive and point source lead emissions into air and water are about 40 to 50 times higher than comparable past loadings from geogenic Vienna. Furthermore, a life cycle approach from acid car batteries indicates that sustainable lead management should consider flows and stocks in the hinterland of the city too. The city metal stock also represents a potential resource. Leaded water pipes built-in in Vienna's city stock have the potential to produce 1.6 million traditional car batteries. In future such city mining strategies can partly replace ore mining.     

Total Lead and Stable Lead Isotopes in Stockholm Sediments

Lead (Pb) in the environment is derived from both naturaland anthropogenic sources. The aim of this study is to estimate the isotopic signature of anthropogenic Pb in sediments from a highly contaminated area (Stockholm), to discuss the influence of different sources on this signature, and to suggest natural Pb background concentrations. Also distribution patterns and differences between different water areas in Stockholm have been studied, both by total Pb and stable Pb isotopes. In 1993, sediment samples were collected at 24 stations in the Stockholm area and analysed for total Pb, zirconium (Zr), scandium (Sc) and stable Pb isotopes (^{204, 206-208}Pb). Total Pb data show that the Stockholm sediments are severely contaminated by Pb. The contamination seems to be rather local since the small lakes surrounding the central parts of Stockholm are much less effected than the central parts. Stockholm is clearly influenced by anthropogenic and natural sources, but in some of the small lakes also by Pb in zircons from the geological basement. The anthropogenic Pb in Stockholm has typical ²⁰⁷Pb/²⁰⁶Pb ratios of 0.85–0.89 and ²⁰⁸Pb/²⁰⁴Pb ratios of 36–38, which are distinct from natural sources. Pb/Sc ratios suggest that the natural background Pb concentration is 10–20 mg kg^-1 d.w.     

Changing of Lead and Cadmium Pools of Swedish Forest Soils

The aims of the paper are to; i)evaluate the rate and direction of present changesin lead (Pb) and cadmium (Cd) soil pools of Swedishforests; ii) discuss processes of importance forleaching of Pb and Cd in Swedish forest soils. Thepresently ongoing changes of Pb and Cd pools ofSwedish forest soils are evaluated by compilationof data from the literature and unpublishedsources. It is concluded that Cd pools arepresently decreasing in larger areas of Sweden. Therate of decrease is mainly determined by soilacidity status; Cd leaching is regulated by ionexchange with Ca²⁺, Mg²⁺, Al³⁺ andH⁺, and is higher in acid soils. The Pb poolsare presently increasing with 0.1 to 0.3 percentannually in the soil down to 0.5 meter. Pb isredistributed from the O horizon to the B horizon,most pronounced in spruce forests; the Pb pools ofthe O horizon are presently not increasing, but isslightly decreasing by 0.1 to 0.2 percent annually. The leaching of Pb in the soil is controlled byfactors regulating the solubility of organicmatter.     

Lead immobilization in mechanochemical fly ash recycling

In previous studies, we focused on a mechanochemical process for recycling fly ash for use in cement; this process was expected to immobilize heavy metals in the fly ash, a desirable outcome in light of the fact that recycled fly ash is commonly used in the synthesis of inorganic materials. Here, we investigated the leaching of lead (Pb) from fly ash treated by a mechanochemical process and from cement prepared from the treated fly ash. We used lead oxide (PbO), a typical Pb compound in fly ash, as a model substance. Mechanochemical treatment of the fly ash inhibited Pb leaching by 93%, and further inhibition (more than 99.9%) was observed in cement produced from the treated fly ash. During the mechanochemical treatment, PbO was reduced to Pb by iron from the stainless-steel mill used for processing, and the lower solubility of Pb in water resulted in immobilization of the Pb.