有关"致癌保鲜膜"问题的探讨

食品保鲜膜应用广泛,影响面大,"致癌保鲜膜"问题在我国掀起轩然大波;介绍食品保鲜膜的主要材质:聚乙烯(PE)、聚氯乙烯(PVC)、聚偏二氯乙烯(PVDC);分析哪些保鲜膜不安全;增塑剂DEHA是否致癌物,为什么有比较安全的PE保鲜膜,商家还要使用存在安全隐患的PVC保鲜膜;为什么有其他合法增塑剂不用,还要用违反国标的DEHA;不加增塑剂的保鲜膜是否绝对安全;保鲜膜能否放在微波炉里加热;有人不敢用保鲜膜,改用塑料袋、微波炉塑料容器了,是否保险.     

东莞市大岭山镇:打造现代生态新城创建全国环境优美乡镇

东临风光迤逦的松山湖,北靠同沙自然保护区,西南依大岭山森林公园,倚山傍湖,生成了大岭山镇的天生丽质.近年来,大岭山镇委、镇政府将建设"依山傍湖的现代生态新城"作为新时期战略目标,在"创建省卫生镇"等一系列工作上,获得喜人成绩.     

打破僵局

"我们拔了18吨,仍不见动静,请领导拿意见."4月13日,当河南油田井下作业二部副经理靳水生和工艺人员赶到L1256井场时,201修井队技术员范红禅立即向他们汇报拔钻解卡情况. "好,再拔拔看!"听到指令,司机汪佳柱启动30吨斜井作业机,一手扶离合器手柄,一手握刹把,脚踩油门,两眼紧盯指挥手势.作业机吼叫着,掐着油管的"脖子"使劲往上拽,那架势如同一场拔河比赛.压力器指针指向了18吨,油管还是一动不动.     

中俄界河黑龙江沿岸地区自然保护区建设和管理研究

随着生产力水平的不断提高和世界经济一体化趋势的快速发展,国际河流已成为有关国家开发的热点,国际河流的生态保护与生态安全是国家维护自身生态安全的前沿.界河--黑龙江流域可持续发展,对边境地区的稳定.防止流域生态退化和保护黑龙江流域森林、黑土地、湿地等资源具有重要意义.界河沿岸地区的自然保护区在保护该地区的生态环境,生物多样性、生态系统功能和国土安全方面起到了非常重要的作用.文章介绍了界河沿岸地区自然保护区的发展状况以及数量、面积、类型、分布和管理等现状,分析了制约自然保护区发展的主要因素提出了因地制宜的建设该地区自然保护区的有效措施及发展方向.     

天津快速的经济发展造成的环境问题及具对策

直面冷峻的环境现状,每一个有理性与责任感的公民无不忧心如焚.蔽日的烟云、腥臭的污河、毒化的农田和振聋发聩的噪音一刻不歇地疯狂考验和鞭笞着人们从心灵到生理的忍耐极限.本文使用大量详实的数据还原出天津环保的真相,社会各界的高度关注、积极参与和成效卓著的努力让我们对天津山清水秀的明日充满了期待.     

浅析电子政务信息的定位及实践

2006年起,广西壮族自治区地震局把做好政务信息工作摆上了重要议事日程,安排了专人负责,落实了措施,落实了专项经费,政务信息工作发生了质的飞跃.特别是信息管理员制度和激励机制从根本上改观了政务信息往日的面貌.本文介绍了广西壮族自治区地震局电子政务信息工作在事业发展中的定位、主要做法、成效和经验,意在抛砖引玉,加强学习和交流.     

上海市交通干道空气中挥发性有机物冬季污染特征研究

2004年冬季对上海市交通干道附近空气中的挥发性有机物进行了连续6天的监测.采用GC-MS定性检出28种物质,芳香烃和烷烃分别占32%和25%.在检出物中有8种属于美国EPA优先控制的有毒有害物质.GC-FID定量表明,芳香烃中含量最高的是苯系物(BTEX)苯、甲苯、乙苯、二甲苯,其中甲苯浓度最高.苯系物的浓度与一氧化碳和二氧化氮的良好相关性说明苯系物的来源与机动车尾气密切相关,而且都受风速和车流量的影响.     

电石渣综合利用研究进展

详细介绍了电石渣在生产建材,治理环境污染,生产化工产品等方面的利用,并对它们在处理效果,创造的经济效益及实际应用过程中遇到的问题进行了分析.提出了一种处理电石渣的有效方法--生产具备高附加值的纳米碳酸钙,在实现经济效益的同时,还能创造良好的环境效益及社会效益.     

"难缠"意味着什么

一次,我国一家工厂想接一位德商的棉布袋订单.对方要求,棉布袋的材料必须是本色棉布,两面的图案须用6种颜色印刷,而且对袋子的尺寸和提手的针脚都作了严格的规定.德商没有当场与这家工厂的厂长签约,而是提出在做出符合标准的样品后,再谈今后的合作.     

惯性(小小说)

每天的17:30分,我们乘坐的班车在下班号响后会准时驶出厂门,出了厂门的右侧有个站,这儿是机关干部的上车点. 由于班车从我们车间始发,近水楼台先得月,我便有了固定的座位,一个位于车尾,靠窗的单座.而每天经过厂门口停站时,总会上来一个人,站在我边上,伸出一只毛茸茸的手抓住扶手.从那一身将校呢的制服上,我了解到他是厂武装部长,姓王,今年初刚转业到我们厂工作.     

电动力和铁PRB技术联合修复铬(Ⅵ)污染土壤

考察了电动力学方法对模拟铬(Ⅵ)污染土壤以及天津市原同生化工厂遗留下的铬渣山周边土壤的修复效果,并将该技术与铁可渗透反应格栅(permeable reactive barrier,PRB)技术联用,找出了较好的联用方式,与单一电动修复进行了对比.研究表明,电动力学技术能有效地修复被铬(Ⅵ)污染的土壤,模拟污染土壤铬(Ⅵ)的去除率达98%～100%,总铬去除率在阳极室附近为80%左右,而阴极室附近则为90%以上,恢复到土壤背景值;铬(Ⅵ)去除的同时伴随着铬(Ⅵ)向铬(Ⅲ)的转化,修复结束时土壤中残留的铬90%以上为铬(Ⅲ);污染极其严重的铬渣山下土,由于含约28%的铬(Ⅲ),修复结束时铬(Ⅵ)的去除率达98%以上,而总铬去除率仅为75%～77%;阳极室附近土壤pH降低而阴极室附近土壤pH升高,处于两极中间位置的pH变化不大.电动力学与铁PRB原位联用方式能充分地利用这2种技术的优点,修复后,土壤任意位置的总铬去除率接近90%,阳极室附近尤为好于单一电动修复,对土壤pH的影响也较小.     

高浓度含铬废水的综合利用

探讨了高浓度含铬褪铜废液的处理方法 ,根据该废液铬含量高 ,具有回收利用价值的特点 ,提出了一条综合利用含铬废液的工艺路线。将含铬废液在合适的条件下把Cr(Ⅲ )氧化为Cr(Ⅵ ) ,加合适的沉淀剂除杂质后 ,加入铅盐溶液 ,生成铬黄     

Response of soil catalase activity to chromium contamination

The impact of chromium(III) and (VI) forms on soil catalase activity was presented. The Orthic Podzol, Haplic Phaeozem and Mollic Gleysol from di erent depths were used in the experiment. The soil samples were amended with solution of Cr(III) using CrCl3, and with Cr(VI) using K2Cr2O7 in the concentration range from 0 to 20 mg/kg, whereas the samples without the addition of chromium served as control. Catalase activity was assayed by one of the commonly used spectrophotometric methods. As it was demonstrated in the experiment, both Cr(III) and Cr(VI) have an ability to reduce soil catalase activity. A chromium dosage of 20 mg/kg caused the inhibition of catalase activity and the corresponding contamination levels ranged from 75% to 92% for Cr(III) and 68% to 76% for Cr(VI), with relation to the control. Catalase activity reached maximum in the soil material from surface layers (0–25 cm), typically characterized by the highest content of organic matter creating favorable conditions for microorganisms.     

风化铬渣与新鲜铬渣中六价铬溶出特性的研究

采用直接淋浸法对风化铬渣及新鲜铬渣进行了六谷铬溶出的条件试验，60min的浸泡时间，80目以下的粒度对渣水比250g/200mL的新渣中Cr(VI)浸出率达69．4％，渣水比250g/200mL,500g/400mL,750g/600mL的风化渣中Cr(VI)的总溶出率分别为70．2％，86．3％，94．0％，其中第一次淋滤溶出率分别达48．1％，70．0％，81．6％，低PH值的淋浸水有利于Cr(VI)的浸出，在PH值为3时溶出率达高峰，Cr（VI）浸出质量比自然条件（近中性）高出14．1％－16．3％，增大管径和降低装置的滤面负荷可提高浸出效果，在直径80mm管径，500g铬渣装填料，滤面负荷9．95g/cm^2时，Cr（VI）溶出率达98．7％，真空抽滤可提高Cr（VI）浸出速率，但降低了滤液中Cr（VI）的浓度和溶出质量，上述试验结果表明了直接淋浸法回收铬渣中六价铬的可行性，并可作为工业化装置的设计参数。     

Elimination of a pollution associated with chromic acid during the electro-deposition of Cr(III) using appropriate anodic and membrane materials in a double film bath

A method using trivalent chromium has been used to replace hexavalent chromium for the electro-deposition of chromium. Using a tri-chamber bath system various anodic materials and membranes were evaluated to minimize the production of environmentally and health damaging chromic acid. By measuring the absorbance of Cr(VI) at 640 nm, the results indicate that the use of a titanium plated ruthenium (Ti-Ru) anode produces the least amount of chromic acid byproduct compared to lead-gold alloy and graphite anodes. The concentration of Cr(VI) in the immediate vicinity of the Ti-Ru anode decreased from 0.389 mg/L to 0 during a 40-min deposition period. The use of a Nafion^TM quaternary cation exchange membrane portioning the buffer and anode selectively prevented Cr(III) from entering the anode compartment whilst allowing the migration of H⁺ to maintain overall voltaic continuity. It has been demonstrated that the use of a Ti-Ru anode with a Nafion^TM membrane can eliminate the production of chromic acid associated with the electro-deposition of chromium plate thereby preventing its health damaging exposure to plant operators and preventing discharge of Cr(VI) into the environment. Addition of a surfactant improved current efficiency by 34.7%.     

Experimental study on Cr(Ⅵ) reduction by Pseudomonas aeruginosa

Investigation on Cr( Ⅵ ) reduction was conducted using Pseudomonas aeruginosa. The study demonstrated that the Cr(Ⅵ) canbe effectively reduced to Cr( Ⅲ ) by Pseudomonas aeruginosa. The effects of the factors affecting Cr( Ⅵ ) reduction rate including carbon source type, pH, initial Cr(Ⅵ) concentration and amount of calls inoculum were thoroughly studied. Malate was found to yield maximum biotransformation, followed by succinate and glucose, with the reduction rate of 60.86%, 43. 76% and 28.86% respectively. The optimum pH for Cr( Ⅵ ) reduction was ?.0, with reduction efficiency of 61.71 % being achieved. With the increase of initial Cr(Ⅵ) concentration,the rate of Cr(Ⅵ) reduction decreased. The reduction was inhibited strongly when the initial Cr(Ⅵ) concentration increased to 157 mg/L. As the amount of cells inoculum increased, the rate of Cr( Ⅵ ) reduction also increased. The mechanism of Cr( Ⅵ ) reduction and final products were also analysed. The results suggested that the soluble enzymes appear to be responsible for Cr (Ⅵ) reduction by Pseudomonas aeruginosa, and the reduced Cr( Ⅲ ) was not precipitated in the form of Cr(OH)3.     

Arsenic and chromate removal from water by iron chips-Effects of anions

The purpose of this study is to estimate the removal efficiency of As and Cr (VI) by one kind of industrial waste — iron chips, as well as to estimate the effects of typical inorganic anions (sulfate, phosphate, and nitrate), and typical organic anions (citrate, oxalate, and humate) on As or Cr (VI) removal. The results showed that 98% of As (V) and 92% of As (III) could be removed from aqueous phase by the iron chips within 60 min. Compared with As species, Cr (VI) was removed much more rapidly and efficiently with 97% of Cr (VI) being removed within 25 min. The removal efficiency for arsenic was in the order: As (III) (sulfate), As (III) (nitrate) or As (III), As (III) (humate), As (III) (oxalate), As (III) (citrate), As (III) (phosphate), and for chromate was in the order: Cr (VI) (sulfate), Cr (VI) (phosphate) or Cr (VI) (nitrate) or Cr (VI) (oxalate), Cr (VI), Cr (VI) (citrate), Cr (VI) (humate). In all the treatments, pH level increased with time except for As (III), the removal of which was either without anions or in the presence of humate or nitrate.     

Study on activated carbon in chromium-containingwastewater treatment by XPS

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硫代硫酸钠、磷酸钠联合处理铬渣中的六价铬

以硫代硫酸钠为还原剂,将铬渣中的六价铬(Cr(VI))解毒转化为三价铬(Cr(III)),并加入磷酸盐作为稳定剂稳定解毒后的铬渣,考察不同反应时间和药剂用量对铬渣中Cr(VI)去除效果的影响.结果表明:硫代硫酸钠可以有效去除铬渣中的Cr(VI),当其与Cr(VI)的摩尔比为理论摩尔比的12倍、处理时间15d时铬渣中Cr(VI)的去除率达到最高(70%),继续增加还原剂用量或延长反应时间均不能有效提高Cr(VI)的去除率.随后加入磷酸钠作为稳定剂,当其物质的量为生成Cr(III)的4倍时,硫代硫酸钠与磷酸钠分步加入(两步法)比同时加入(一步法)处理铬渣的效果较好,处理效果最好时总铬浸出浓度为6.1mg/L,低于危险废物浸出鉴别的总铬标准(15mg/L),而且形成稳定的铬的化合物(CrPO4·6H2O).铬渣pH值变化、五态变化、XRD及XPS分析等结果表明,两步法的处理效果好于一步法.     

可渗透反应复合电极法对铬(Ⅵ)污染土壤的电动修复

将Fe0、沸石等活性材料附着在电极上构成可渗透反应复合电极,以Cr(Ⅵ)污染土壤为处理对象,对电动修复过程中可渗透反应复合电极法对土壤pH的控制、Cr的去除效果以及形态变化进行了研究.结果表明,添加可渗透反应材料的复合电极法比单一电极法无论在土壤pH控制还是Cr的去除方面都有明显的改善和提高,其中以在阳极同时添加Fe0和沸石效果最为显著.在施加2 V.cm-1的直流电压,运行5 d后,相比在阳极单纯添加沸石或Fe0可渗透反应层,添加"Fe0+沸石"反应层能在最大程度上减小阳极土壤pH值的波动,可将土壤pH值控制在5.5～8.5范围内,土壤中任意位置Cr(Ⅵ)的去除率可提高到97%以上,土壤中残留的Cr(Ⅲ)更少,可渗透反应层对Cr的截留量可分别提高8倍和1.8倍,并将98%的Cr(Ⅵ)转化为低毒的Cr(Ⅲ).研究结果为开发具有实用意义的可渗透反应复合电极修复技术提供了理论依据.