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。     

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.     

不同氯离子浓度对电化学法处理微污染水中含氮化合物的影响

采用电化学氧化法对微污染水进行处理,在极板间距为1 cm,电解时间为10 min的条件下,通过投加NaCl溶液,使水中的NH4+及Cl-的摩尔比分别为1∶1、1∶2、1∶3,并与未投加NaCl溶液的电解出水进行比较,主要考察不同氯离子浓度对电化学法去除微污染水中的含氮化合物的效果影响.实验表明:随着氯离子浓度的不断提高...     

联合硅藻土与PAC强化混凝处理含藻微污染原水

研究了联合硅藻土与聚合氯化铝（PAC）强化混凝对原水中藻类、溶解性有机物以及重金属离子的去除效果。结果表明,硅藻土的投加可以有效地改善絮体的沉降性能,增强藻类的混凝沉淀去除效率,PAC投加量为30 mg/L时,投加0.1 g/L硅藻土,叶绿素a去除率由82.5%提高到95.9%。该强化混凝过程使原水中溶解性有机物特别是大分子有机物和重金属离子的去除率有所上升。PAC投加量为30 mg/L,硅藻土投加量为1.5 g/L时,重金属Cu、Pb和Cd的去除率分别达到57.5%、83.7%和22.2%。     

复合絮凝剂APAC中铝形态分布及絮凝性能研究

用慢速滴碱法合成聚合氯化铝的过程中加入酸改性的凹凸棒,制备了新型絮凝剂APAC。采用Al-Ferron逐时络合比色法和烧杯絮凝实验法分别研究了APAC复合絮凝剂中铝的形态分布和絮凝性能。结果表明,Ala随盐基度的升高而逐渐降低;Alb随盐基度的升高而升高;Alc则先随盐基度的升高而升高,达到最大值后,再随盐基度的升高而降低。在相同实验条件下,盐基度愈高,混凝效果愈好,Alb含量愈高,混凝效果并不一定愈好。因此,APAC的质量控制以及追求目标应当是尽量提高Alc的含量,而不是Alb的含量。     

纳米SiO2对微污染物HA、SDS及NH3-N的助凝特性研究

以聚合氯化铝PAC为混凝剂,纳米SiO₂为助凝剂,对含有下列微污染物：十二烷基硫酸钠（SDS）、氨氮（NH₃-N）或腐植酸（HA）的高岭土悬浊液进行混凝沉降实验。借助形态学理论、电镜观察与图像分析技术,研究纳米SiO₂对微污染物的助凝作用效果、吸附特性与絮体结构的形态学特征。结果表明：（1）在含有HA、SDS、NH₃-N的模拟原水中,污染物去除率与浊度去除率的相关性随污染物分子量的增大而增强;（2）纳米SiO     

Effects of N-acetyl-L-cysteine on fish hepatoma cells treated with mercury chloride and ionizing radiation

Organisms are exposed to natural radiations from cosmic or terrestrial origins. Furthermore the combined action of radiation with various chemicals is an inevitable feature of modern life. Radiation is known to cause cell death, mainly due to its ability to produce reactive oxygen species in cells. N-acetyl-l-cysteine (NAC) is a well-known sulfhydryl-containing antioxidant whose role in radioprotection has been reported. Synergistic effects of radiation and mercury chloride on human cells was previously reported by the authors. Based on the previous report, this study was designed to assess the synergistic effects of radiation and mercury chloride on fish hepatoma cells, as well as to investigate the protective effects of NAC on the cells. The cytotoxicity of radiation was enhanced in the presence of mercury chloride. NAC in lower concentrations prevented cells from death after irradiation with lower doses (<300 Gy) while it did not prevent cells from radiation-induced death after irradiation with higher doses (300, 500 Gy). The intracellular glutathione (GSH) levels significantly decreased after irradiation while the combined treatment of NAC and radiation alleviated the decrease in the GSH levels. The investigations give a clue for the action mechanism of synergistic or protective effects of NAC on the cells. Due to their high resistance to ionizing radiation, the PLHC-1 cells can be effectively used as a screening tool for assessing the combined effects of radiation with toxic chemicals.     

可再生湿法烟气脱硫过程有机胺吸收液中硫酸根的测定

为了快速准确测定可再生湿法烟气脱硫过程有机胺吸收液中的p(SO2-4),建立了以茜素红为指示剂,用BaCl2直接滴定测定有机胺吸收液中p(SO2-4)的方法.实验结果表明:当试样pH为4.0 ～4.5时,方法的相对误差为0.28％-0.62％,加标回收率均在97％以上;SO2-3的存在会使p(SO2-4)的测定结果偏大...     

含镍三氯化铁蚀刻废液的综合利用

针对显像管荫罩生产工艺中产生的含镍三氯化铁蚀刻废液的处理,先用铁粉将 3价的铁还原,再以硫化亚铁将镍置换回收镍,而铁以液体三氯化铁或固体氯化亚铁的形式得到综合利用,处理工艺技术先进、简单有效,环境效益及经济效益显著。     

Al3+对序批式生物膜反应器(SBBR)中污泥脱氢酶活性(DHA)和胞外聚合物(EPS)的影响

通过向序批式生物膜反应器(SBBR)中投加氯化铝,研究了化学协同生物除磷过程中Al~(3+)对污泥脱氢酶活性(DHA)、胞外聚合物(EPS)及系统处理效果的影响.结果表明,氯化铝投加量少于0.1 mmol·L~(-1)时,Al~(3+)对微生物的活性有促进作用,多于0.1 mmol·L~(-1)的Al~(3+)对其活性有明显的抑制作用.氯化铝投加量少于0.1 mmol·L~(-1)时,Al~(3+)能够促进EPS中多糖(PS)和蛋白质(PN)的分泌,多于0.1 mmol·L~(-1)的Al~(3+)则只促进多糖的分泌,但对EPS的分泌总量没有影响.Al~(3+)会使污泥的SVI值显著降低,大大改善其沉降性能.MLSS、MLVSS基本上是随着Al~(3+)投加量的增加而增大,MLVSS/MLSS随着投药量的增加先减小后增大再减小.Al~(3+)对COD和TN的去除具有轻微抑制作用,但对TP的去除具有显著的改善作用.当Al~(3+)的投加为0.5 mmol·L~(-1)时,TP的去除效果最好,出水浓度仅为0.44 mg·L~(-1),满足一级A排放标准.此时,TP的去除率为92.7%,比不加药时提升了10.2%.