高聚聚硫氯化铝混凝去除水中腐殖酸

采用快速加碱法制备了分别以Al13和Al30为主要水解形态的聚合氯化铝PAC-Al13和高聚聚合氯化铝PACAl30。通过向PAC-Al30中引入SO2-4/Al3+摩尔比为0.06的SO2-4离子,制得高聚聚硫氯化铝SPAC-Al30。激光散射粒径分析以及Ferron逐时络合比色结果表明,加入SO2-4后SPAC-Al30的平均粒径增大为4.85 nm,高聚合水解形态Alc含量分别比PAC-Al13和PAC-Al30提高52.7%和17.5%。ζ电位分析以及烧杯混凝实验结果表明,SPAC-Al30的电中和能力不及PACAl30和PAC-Al13,混凝去除水中腐殖酸的效果却有显著提高,且由于SPAC-Al30较为温和的电中和性能,在混凝剂投量较高时不易出现再稳现象。SPAC-Al30的纳米级分子尺寸和高聚合水解形态有利于其发挥更优的吸附架桥和网捕卷扫作用,SPAC-Al30是去除水中腐殖酸的一种新型高效混凝剂。     

长链季铵盐的絮凝性能

采用FTIR技术对自制的长链季铵盐絮凝剂环氧丙基十二烷基二甲基氯化铵进行了表征,研究了该絮凝剂对高岭土悬浊液的絮凝效果,考察了絮凝剂加入量、溶液pH和絮凝时间对絮凝率的影响;并与常用絮凝剂聚丙烯酰胺的絮凝效果进行了对比。表征结果显示,合成的目标产物为环氧丙基十二烷基二甲基氯化铵。实验结果表明：在絮凝剂加入量8 mg/L、溶液pH 9、絮凝时间50 min的条件下,絮凝率达到84.84%;在相同絮凝剂加入量的条件下,环氧丙基十二烷基二甲基氯化铵的絮凝效果优于聚丙烯酰胺。     

模拟氯化钠盐渣的高温处理

采用高温处理法对模拟氯化钠盐渣（简称盐渣）进行处理,研究了加热过程中气体有机物产生量随加热时间的变化规律以及加热温度对气体有机物产生量的影响,并分析了盐渣的高温处理效果。实验结果表明：含苯盐渣、含异丁醇盐渣、含氯苯盐渣、含二甲苯盐渣和混合盐渣在高于盐渣中所含有机物沸点30 ℃的条件下加热120 min,盐渣中的有机物去除率均大于99.99%;混合盐渣的加热温度越高,气体有机物的产生速率越快,相同时间内有机物的去除率也越大;盐渣中有机物的气化分离可分为3个阶段,初始阶段有机物气化速率较小,中间阶段气体有机物产生量迅速增加,最后阶段大部分有机物从盐渣中气化分离;盐渣中的有机物在高温气化时,会发生一定的化学反应,有微量的新物质生成。     

电石法聚氯乙烯生产行业的汞污染防治

结合我国电石法聚氯乙烯生产行业的发展现状,提出了采用低汞触媒替代高汞触媒以降低汞消耗、开发高效除汞器以提高脱汞效率、深度解吸废盐酸以解决汞转移问题、深度处理含汞废水以实现综合利用、优化工艺控制以降低汞触媒消耗、改善防护措施以减轻汞扩散等汞污染防治工作的要点。     

氯化锌法改性小麦秸秆制备生物碳质吸附剂及其对磷酸根的吸附效果

为实现农作物秸秆资源化,解决水体富营养化问题,将小麦秸秆化学改性成一种可以有效吸附水体中磷酸根的生物碳质吸附剂,重点考察了氯化锌法改性小麦秸秆制备生物碳质吸附剂的最佳工艺条件以及产品对水体中磷酸根的去除效果。结果表明,当氯化锌溶液质量浓度为250 g/L、浸渍比为2.2∶1、活化温度为600℃、活化时间为45 min时,所得的小麦秸秆生物碳质吸附剂的得率为37.85%,对磷酸根的去除率为99.33%。     

循环流化床灰制备聚合双酸铝铁絮凝剂

为了提高循环流化床灰(CFB灰)的资源综合利用率对CFB灰制备聚合双酸铝铁(PAFCS)的可行性及工艺参数进行了研究,提出了以酸浸、水解、聚合和熟化等工艺过程,制备PAFCS混凝剂产品。重点对制备PAFCS絮凝剂的工艺参数进行研究,并利用红外光谱分析技术对PAFCS进行了结构表征及实验了PAFCS絮凝性能。结果表明,在相同条件下PAFCS的絮凝效果明显好于聚合氯化铝(PAC),用CFB灰制备PAFCS絮凝剂产品是可行的。     

活性污泥焚烧过程中镍的迁移分布特性

采用管式炉对污水厂活性污泥焚烧过程中Ni的迁移分布特性进行研究。实验结果表明：当污泥掺烧量（污泥质量与煤和污泥总质量的比）为25%时,Ni的挥发率（飞灰与气体中Ni质量的总和与污泥中Ni质量的比）几乎为零,且污泥与煤混合试样的综合燃烧效果最好;当污泥焚烧加入硫化物时,各种硫化物对Ni的残留率（炉渣中Ni的质量与污泥中Ni质量的比）提高能力大小顺序为Na₂S>S>Na₂SO₃>Na₂SO₄;当污泥焚烧加入氯化物时,促使Ni向烟气中迁移,且加入无机氯更易使Ni向烟气中迁移。     

Synergistic increase in cell lethality by dieldrin and H2O2 in rat thymocytes: Effect of dieldrin on the cells exposed to oxidative stress

Dieldrin, one of persistent pesticides, is highly resistant to biotic and abiotic degradation. It is accumulated in organisms. Recent studies suggest that dieldrin exerts a potent cytotoxic action on cells exposed to oxidative stress. In this study, the effect of dieldrin on rat thymocytes exposed to hydrogen peroxide (H₂O₂)-induced oxidative stress was examined. Dieldrin at 5 μM and H₂O₂ at 300 μM slightly increased cell lethality from a control value of 5.4 ± 0.5% (mean ± standard deviation of four experiments) to 7.8 ± 1.3% and 9.0 ± 0.3%, respectively. Simultaneous application of dieldrin and H₂O₂ significantly increased cell lethality to 46.2 ± 1.8%. The synergistic increase in cell lethality was dependent on dieldrin concentration (0.3–5 μM) but not on H₂O₂ concentration (30–300 μM). Dieldrin accelerated H₂O₂-induced cell death, which was estimated with the help of annexin V-FITC and propidium iodide. Presence of either dieldrin or H₂O₂ decreased the cellular content of nonprotein thiol and increased intracellular Zn²⁺ concentration. The combination of dieldrin and H₂O₂ further pronounced these effects. TPEN, a chelator of intracellular Zn²⁺, significantly attenuated the synergistic increase in cell lethality induced by dieldrin and H₂O₂. It is, therefore, suggested that dieldrin augments the cytotoxicity of H₂O₂ in a Zn²⁺-dependent manner.     

Controlled release formulations of metribuzin: Release kinetics in water and soil

Controlled release (CR) formulations of metribuzin in Polyvinyl chloride [(PVC) (emulsion)], carboxy methyl cellulose (CMC), and carboxy methyl cellulose-kaolinite composite (CMC-KAO), are reported. Kinetics of its release in water and soil was studied in comparison with the commercial formulation (75 DF). Metribuzin from the commercial formulation became non-detectable after 35 days whereas it attained maxima between 35–49 days and became non-detectable after 63 days in the developed products. Amongst the CR formulations, the release in both water and soil was the fastest in CMC and slowest in PVC. The CMC-KAO composite reduced the rate of release as compared to CMC alone. The diffusion exponent (n value) of metribuzin in water and soil ranged from 0.515 to 0.745 and 0.662 to 1.296, respectively in the various formulations. The release was diffusion controlled with half release time (t_1/2) from different controlled release matrices of 12.98 to 47.63 days in water and 16.90 to 51.79 days in soil. It was 3.25 and 4.66 days, respectively in the commercial formulation. The period of optimum availability of metribuzin in water and soil from controlled released formulations ranged from 15.09 to 31.68 and 17.99 to 34.72 days as against 5.03 and 8.80 days in the commercial formulation.     

山东省环境应急演练污染标示物释放实验

山东省环境应急演练要求投放污染标示物进行真实性监测。为了保证演练顺利开展,选择三氯化铁作为污染标示物,在胜利河郭家桥—四马桥11.34 km河段进行了释放实验。实验结果证明三氯化铁做标示物是可行的,并对三氯化铁的释放流量、演练需用量和河段的沉降系数进行了确定。