四川省酸雨时空分布特征

通过对四川省能源结构和废气排放情况的分析,结合四川省近年来酸雨监测资料,包括年平均降水pH值、酸雨频率,总结了近年来四川省酸雨的时空分布特征。通过对降水离子的分析,说明四川省酸雨阴阳离子的组成,酸雨为硫酸型,各城市之间存在致酸物质的远距离输送和相互影响。将2006年四川省酸雨状况与2005年状况进行比较,并且对酸雨污染程度进行分级,结论是2006年四川省部分城市酸雨污染形势趋于加重,全省酸雨污染形势仍然严峻,并提出了控制酸雨的对策措施。     

常德市酸雨化学特征、趋势分析及控制对策

常德市是中南地区酸雨污染最为严重的城市之一。以常德市2004年至2006年的降雨连续监测数据为基础,应用统计学相关分析的方法,对常德市158次降雨的变化特征进行了分析和研究。结果表明,常德市降雨酸度呈波动性变化,近3年的降雨pH年均值都在5．4以下,对降雨中离子含量的分析可知,酸雨主要为硫酸型,有向硫酸和硝酸混合型转化的趋势。降雨中的主要离子浓度和通量在冬、春季节高于夏、秋季节,降雨中阴阳离子极不平衡,[SO4^2-]和[Ca^2＋]浓度对降雨离子的平衡有较大的影响。常德市的净酸度沉积量在2004年高达199．29meq m^-2yr^-1,而从2004年-2006年,净酸度沉积量和离子沉降总通量均在逐年降低,表明常德市降雨酸化现象有所缓和．     

鼎湖山酸性土壤中放线菌数量与酸度的关系

本文报导鼎湖山几种赤红壤土壤放线菌的分布与酸度的关系。不同酸度培养基计数结果表明,土壤放线菌数量主要决定于适应在中性环境中生长的类型,适于酸性、强酸性环境生长的类型的数量很少。     

酸雨和降尘对菜青虫生长和取食行为的影响

通过室内模拟试验探讨了酸雨、降尖及其复合污染对菜青虫生长发育和取食行为的影响。结果表明，直接处理对菜青虫有明显的抑制作用，而间接处理则有促进作用。试验发现，在受污染的植物体内有糖分与蛋白质积累现象，这是造成虫害加重的主要原因之一。     

模拟酸雨及A1^3＋共同作用对蚕豆根尖细胞的遗传损伤

以蚕豆为材料，研究了模拟酸雨及酸雨与铝共同作用的细胞遗传学效应．结果表明，根尖细胞有丝分裂指数随Al^3＋浓度的升高和环境酸度的增强而下降；处理组细胞中出现了多种染色体异常，如染色体粘连、滞后及断裂等．模拟酸雨及其与低浓度Al^3＋（3mg／L）共同作用时可诱发蚕豆根尖细胞微核，其中pH4．5组微核率高于pH3．5组．模拟酸雨与高浓度的Al^3＋（10～180mg／L）复合处理可引起根尖细胞固缩，固缩率随Al^3＋浓度增加和pH降低而增高．研究结果表明，pH4．5和pH3．5的模拟酸雨和Al^3＋对蚕豆根尖细胞具有遗传损伤作用，其效应与Al^3＋浓度和环境酸度有关．     

模拟酸雨对珍稀濒危植物红豆杉幼苗的影响研究

利用模拟酸雨实验对珍稀濒危植物曼地亚红豆杉和南方红豆杉生长及生理生化指标进行研究。结果表明,pH4.5的模拟酸雨促进了曼地亚红豆杉(Taxus media)和南方红豆杉(T.mairei)的株高生长(与对照相比分别促进了19%和72%),pH3.5的模拟酸雨对其有一定的影响,但不显著。pH4.5和pH3.5的酸雨处理下,曼地亚红豆杉基径比对照分别下降了46%和42%;南方红豆杉的相应值分别是34%和43%。总的来说,模拟酸雨促进了这两种红豆杉叶绿素的质量分数,类胡萝卜素的质量分数变化因种而异。酸雨处理提高了曼地亚红豆杉抗氧化系统酶活性,与对照相比约提高了5%～142%;南方红豆杉的相应值为-16%～35%。曼地亚红豆杉游离脯铵酸和丙二醛(MDA)的质量分数比对照提高了13%～73%;而南方红豆杉的相应质量分数基本等于或低于对照。与南方红豆杉相比,曼地亚红豆杉对酸雨更加敏感。     

模拟酸雨及Al3+共同作用对蚕豆根尖细胞的遗传损伤

以蚕豆为材料,研究了模拟酸雨及酸雨与铝共同作用的细胞遗传学效应.结果表明,根尖细胞有丝分裂指数随Al3 浓度的升高和环境酸度的增强而下降;处理组细胞中出现了多种染色体异常,如染色体粘连、滞后及断裂等.模拟酸雨及其与低浓度Al3 (3mg/L)共同作用时可诱发蚕豆根尖细胞微核,其中pH4.5组微核率高于pH3.5组.模拟酸雨与高浓度的Al3 (10～180mg/L)复合处理可引起根尖细胞固缩,固缩率随Al3 浓度增加和pH降低而增高.研究结果表明,pH4.5和pH3.5的模拟酸雨和Al3 对蚕豆根尖细胞具有遗传损伤作用,其效应与Al3 浓度和环境酸度有关.     

Acid mine-drainage toxicity testing

The BOD inhibition test, the activated sludge respiration inhibition test, and the Microtox® Bioassay procedure were examined for their potential as rapid toxicity screening methods for acid mine drainage (AMD) and for setting toxicity threshold levels in receiving waters. The BOD inhibition test proved to be unsuitable due to the high chemical oxygen demand of the toxicant. The long incubation time (minimum 5 d at 20°C) allowed growth of chemo-autotrophic bacteria and resulted in excessive flocculation and precipitation of metals, making accurate and meaningful measurements of inhibition impossible. The activated sludge respiration inhibition test was successful in measuring AMD toxicity, and for deriving toxicity threshold levels for the basic heterotrophic community in surface waters. However, it is a very time-consuming technique and is not sensitive enough to be used as a routine screening technique. The variability in toxicity was found to be due to the availability of metals as well as the effect of pH on metabolism. Simple linear models were derived to estimate inhibition within surface waters. Prediction of the inhibition caused by AMD can be made as long as the pH of the river water after mixing and the dilution of the AMD are known. Most accurate predictions are made using equations for specific pH ranges, but a useful estimation of inhibition can be obtained using the general equation: inhibition (%) = -2.34 pH + 6.41 AMD (%) + 22.1. The Microtox® Bioassay method, although expensive, was rapid and simple to use. It was the most sensitive test of the three, with the toxic response of marine bacteria increasing notably from 5 to 15 min due to the presence of bivalent metals in the toxicant. The problem of repeatability and reproducibility encountered with the activated sludge inhibition test was overcome with the highly standardised Microtox® method, making it an ideal screening method for AMD. However, the advantage of the activated sludge inhibition test is that the types of heterotrophic micro-organisms found in activated sludge are similar to those found in receiving waters such as the Avoca River and so more meaningful toxicity threshold values can be obtained.     

废旧镍镉电池的生物沥滤处理——沥滤停留时间的影响研究

用污泥加硫酸化液沥滤镍镉电池中的重金属是一种全新的工艺,该工艺主要由生物酸化反应器和金属沥滤反应器两个反应器组成.生物酸化反应器中产生的酸液就是沥滤电池中重金属的反应液.研究表明,酸化液在沥滤反应池的停留时间对沥滤的效果有显著影响.在1、4、7、12 d 4个停留时间中,4 d的效果是最好的,对金属Cd和Ni都用40 d左右基本实现了全部滤除;1d略微慢一些,Cd用了40 d,Ni用了45 d;7 d和12 d的沥滤时间都长于50 d.4 d产生的金属废液量是1 d的1/4,考虑到后续处理金属沥滤废液的工作量,选择4d的停留时间要优于1d.     

Simulation investigations on the marble deterioration by sulphur dioxide

This paper deals with investigations on corrosion of marble SO2. We have simulated oxidation of SO2 by photochemical process in the atmosphere. The experiments indicate that formation of SO3 aerosols is related to the concentration of SO2, the UV light intensity, the time of irradiation and the humidity of the air. The corrosion feature of surfaces of the marble and the depth profiles of sulphur were obtained by SEM (Scanning electron microscope), EDXA (Energy-dispersive X-ray analyzer) and SIMS (Secondary ion mass spectrometer). The results of experiments show the corrosive extent of marble depends on its compositions and microareas of marble, which contain lower silicon content can be easily corroded by SO2.