论有效实施船舶污染应急计划的关键问题

根据《ＯＰＲＣ公约》的要求，船舶、码头、港口、地区、区域、国家都应制订相应的船舶污染应急计划，通过分析各层次应急计划的核心和应急反应体系的组成，指出了有效实施污染应急计划的关键问题。     

电动汽车与燃油汽车的环境指标比较

对燃油汽车的尾气直接污染，尾气间接污染和噪声污染的环境指标进行了分析。比较了电动汽车与燃油汽车的同类环境指标，指出中国发展电动汽车对于改善环境的重要作用。     

铬渣的细菌解毒实验研究

采用从铬渣堆埋场附近的污泥中分离到的高效还原Cr(Ⅵ)的Ch-1菌进行细菌浸出的摇瓶实验,分别考察了不同液固比,温度,初始pH值情况下浸出液的pH值变化,Cr(Ⅵ)浓度变化及浸出过程铬渣中六价铬的浸出率变化和最终渣浸出毒性.实验结果表明,在细菌的作用下,浸出液Cr(Ⅵ)浓度均能解毒为0ppm,同时,浸出液pH值降低到8～9之间, 细菌浸出渣毒性降低到0.05ppm以下,远低于GB5085.3-1996危险废物浸出毒性鉴别标准1.5ppm.同时,渣中的Cr(Ⅵ)也大部分被有效浸出后还原为Cr(Ⅲ) 沉淀.特别是在液固比10:1,温度28℃,初始pH＝10.0的条件下,铬渣中六价铬浸出率达到了95.43%,同时浸出液pH值＝8.20,Cr(Ⅵ)浓度为0ppm,浸出渣浸出毒性0.007 ppm,均达到国家排放标准,取得了较好的解毒效果.     

改善AA1100空调箔强韧性生产工艺的研究

研究了改善AA1100空调箔强韧性的生产工艺。结果表明，采用合理的均匀化工艺，230-260℃×1h成品退火，并尽可能提高退火加热速度，有助于AA1100空调箔达到最佳的强韧性效果。同时，对空调箔的强韧化机理进行了探讨。     

磁化技术在含酚废水处理中的应用

将磁化技术与含酚废水的处理过程相结合。实验结果表明，应用磁化技术能够明显地改善絮凝氧化法处理含酚废水的效果，提高去酚率。     

鸭绿江口的溶解无机氮

本文讨论了１９９６年５月鸭绿江溶解无机氮的含量和分布变化特征，并同其他一些河口作了比较，鸭绿江口ＮＯ３－Ｎ，ＮＯ２－Ｎ，ＮＨ４－Ｎ的平均含量分别为５０．３．０．４５和３．０５μｍｏｌ／Ｌ，而丹东上游鸭绿江支流瑗河下降的溶解无机氮浓度很高，达２０３．４μｍｏｌ／Ｌ，主要由农业施用氮肥大量从耕用地中流失所致。     

Significant tipping points of sediment microeukaryotes forewarn increasing antibiotic pollution

Antibiotic pollution imposes urgent threats to public health and microbial-mediated ecological processes. Existing studies have primarily focused on bacterial responses to antibiotic pollution, but they ignored the microeukaryotic counterpart, though microeukaryotes are functionally important (e.g., predators and saprophytes) in microbial ecology. Herein, we explored how the assembly of sediment microeukaryotes was affected by increasing antibiotic pollution at the inlet (control) and across the outlet sites along a shrimp wastewater discharge channel. The structures of sediment microeukaryotic community were substantially altered by the increasing nutrient and antibiotic pollutions, which were primarily controlled by the direct effects of phosphate and ammonium (−0.645 and 0.507, respectively). In addition, tetracyclines exerted a large effect (0.209), including direct effect (0.326) and indirect effect (−0.117), on the microeukaryotic assembly. On the contrary, the fungal subcommunity was relatively resistant to antibiotic pollution. Segmented analysis depicted nonlinear responses of microeukaryotic genera to the antibiotic pollution gradient, as supported by the significant tipping points. We screened 30 antibiotic concentration-discriminatory taxa of microeukaryotes, which can quantitatively and accurately predict (98.7% accuracy) the in-situ antibiotic concentration. Sediment microeukaryotic (except fungal) community is sensitive to antibiotic pollution, and the identified bioindicators could be used for antibiotic pollution diagnosis.     

NOAA卫星监测巢湖蓝藻水华的试验分析

采用实地水质采样分析、水面光谱测量等实地监测 ,并结合NOAA气象卫星遥感信息 ,对巢湖水华进行星地同步调查监测。结果表明 ,蓝藻叶绿素的存在使得进入近红外波段水体反射率明显上升 ,基于这一光谱特性以及蓝藻特有的漂浮特性 ,可利用NOAA卫星监测巢湖等内陆大面积的严重污染湖泊蓝藻水华的分布状况。     

Membrane fouling control by ultrasound in an anaerobic membrane bioreactor

In this study, ultrasound was used to control the membrane fouling online in an anaerobic membrane bioreactor (AMBR). Short-term running experiments were carried out under different operating conditions to explore feasible ultrasonic parameters. The experimental results indicated that when the crossflow velocity was more than 1.0 m/s, membrane fouling could be controlled effectively only by hydrodynamic methods without ultrasound. When ultrasound was applied, an ultrasonic power range of 60–150 W was suitable for the membrane fouling control in the experimental system. The experimental results showed that the membrane fouling was controlled so well that membrane filtration resistance (ΣR) could stay at 5 × 10¹¹ m^?1 for more than a week with the crossflow velocity of 0.75 m/s, which equaled the effect of crossflow velocity of more than 1.0 m/s without ultrasound.     

产耐温蛋白酶苏云金芽孢杆菌FS140液体发酵条件优化

应用快速有效的数学统计方法对苏云金芽孢菌FS140耐温蛋白酶的发酵条件进行优化.首先采用二水平Plackett-Burman设计对影响产酶的8因素进行筛选,获得培养基成分中3个重要影响的因子:黄豆饼粉、酵母粉、葡萄糖;再利用响应面分析法对该3个因素进行3水平的优化,获得它们的最佳组合:黄豆饼粉1.8%、酵母粉0.36%、葡萄糖0.14%.优化后产酶水平达到837.71U mL-1,与响应面数学模型的预测值只有1.34%的误差.同时进行了发酵温度、初始pH、摇瓶装量与接种量等发酵条件的优化,FS140最终发酵产酶水平达918.91U mL-1.图2表5参14