久效磷对海洋微藻毒性机理的初步研究Ⅲ.超氧化物歧化酶和过氧化物酶活性的变化

报道了久效磷对３种海洋微藻细胞内２种清除活性氧的关键性酶－超氧化物歧化酶和过氧化酶活性的影响。结果显示：１．在久效磷的胁迫下，扁藻和三角褐指藻细胞的超化物歧化酶活性均表现出下降的总变化趋势，而叉鞭金藻细胞的ＳＯＤ活性时而上升，时而下降，在整个胁迫过程中呈现出无规律性的变化。２．随着久铲磷胁迫时间的延长，３种微藻细胞的过氧化酶活性均逐渐下降，表现出相同的变化规律性。     

炼油装置运行周期评估技术及应用

炼油装置运行周期评估技术通过统计、分析装置故障数据,计算特定时间段装置的可靠性,进而获得装置可靠性随时间的变化规律和装置可靠性最差设备排序。介绍了该技术在某常减压装置的应用,应用结果表明,该评估技术为科学确定炼油装置运行周期提供了决策依据。     

Integrated environmental assessment and pollution prevention in Vietnam: the case of anthracite production

Using the concept of life cycle analysis, the whole life cycle of anthracite production in Vietnam was assessed and the environmental “hot-spots” were identified. These include (i) dust pollution at coal transfer points or piles in storage; (ii) noise pollution resulting from the usage of heavy equipment, and (iii) high volume of acid and turbid mine water discharged into the environment.Pollution prevention and treatment options were identified and discussed in this study which consists of wet treatment of dust, planning, collection and treatment of mine water, planting of trees for dust and noise reduction as well as minimization of erosion. Some recommendations are made for pollution abatement from coal production and improvement of anthracite production in the region.     

SBR工艺处理维生素C废水试验研究

采用颗粒污泥和普通絮体污泥SBR反应器对维生素C生产废水进行可生化性对比试验研究，结果表明，在进水CODcr为400—1800mg／L，运行周期为8h，其中曝气时间为5．5h，换水比为80％的条件下，颗粒污泥反应器CODer去除率为75-90％，污泥浓度介于6．11～8．32g／L，污泥指数为20～40mL／g.     

Enhanced removal of high-As(Ⅲ) from Cl(-Ⅰ)-diluted SO4(-Ⅱ)-rich wastewater at pH 2.3 via mixed tooeleite and(Cl(-Ⅰ)-free) ferric arsenite hydroxychloride formation

An advanced cost-saving method of removal of high-As(Ⅲ) from SO₄(-Ⅱ)-rich metallurgi cal wastewater has been developed by diluting the SO₄(-Ⅱ) content with As(Ⅲ)-Cl(-Ⅰ)-rich metallurgical wastewater and then by the direct precipitation of As(Ⅲ) with Fe(Ⅲ) at pH2.3.As(Ⅲ) removal at various SO₄(-Ⅱ)/Cl(-Ⅰ) molar ratios and temperatures was investigated The results showed that 65.2–98.2%of As(III) immobilization into solids occurred at the SO₄(Ⅱ)/Cl(-Ⅰ) mo...     

辛基酚的体内类雌激素活性评价

利用体内大鼠子宫增重试验检测辛基酚（OP）的类雌激素活性，并对其观测终点及影响因素进行了初步研究。结果显示，OP经大鼠体内染毒，可引起大鼠子宫湿重、子宫内皮细胞厚度、子宫腺数量明显增加，具有明显的类雌激素活性。三条染毒途径检测敏感度腹腔染毒＞经皮下染毒＞经灌胃染毒。     

生物活性炭处理废水中有机物的研究探讨

生物活性炭(BAC)是一种处理有机废水的有效方法。现以BAC处理废水中的酚和甲醇为例,综述BAC处理废水中有机物的机理和影响因素。并通过生物活性炭吸附降解四氯乙烯(PCE)的综合模型得到BAC作用与吸附和生物降解的关系。最后简单介绍了BAC中活性炭与微生物的选择。     

Effects of alternating temperatures on development and reproduction of the armyworm,Mythimna separata (Walker)

Effects of cycling and constant temperature on development and reproduction of the armyworm, Mythimna separata (Walker) were investigated by rearing the insects on the artificial diet under temperatures covering low(16-24℃ vs. 20 ℃ ), medial(20-28℃ vs. 24℃ ) and high(24-32 ℃ vs. 28 ℃) regions. In the low region, all the immature stages of the insect developed significantly faster under alternating temperatures than at corresponding constant temperatures. For the medial region, their development was little affected by variable temperatures. For the high region, developmental durations tended to be longer under cycling temperatures except egg stage.Mean fecundities of the adult moths markedly increased under cycling temperatures as compared with those at respective constant temperature in all regions.Possible reasons for effect of alternating temperatures on insect development are discussed in some details.     

两种奥氏体不锈钢酸性盐雾腐蚀行为研究

目的研究0Cr18Ni9(钝化)不锈钢与0Cr18Ni10Ti(钝化)不锈钢在酸性盐雾条件下的腐蚀行为,为发动机零件选材及防护措施的改进提供依据。方法按GJB150.11A—2009《军用装备环境试验方法盐雾试验》进行,调节溶液p H到3.5±0.5,以24 h喷雾润湿+24 h干燥为一个循环,分别开展2(96 h)、4(192 h)、5(240 h)个循环的酸性盐雾试验。采用目视、称量、X射线衍射(XRD)、扫描电子显微镜(SEM)及能谱仪(EDS)对盐雾腐蚀后试样进行观察及分析。结果 0Cr18Ni9(钝化)与0Cr18Ni10Ti(钝化)两种奥氏体不锈钢均发生了轻微的腐蚀,主要为局部腐蚀及均匀腐蚀。结论两种金属在酸性盐雾条件下耐蚀性良好,且可满足目前海军型发动机对材料耐酸性盐雾腐蚀的要求,0Cr18Ni9(钝化)略优于0Cr18Ni10Ti(钝化)。     

基于行业全产业链评估一份外卖订单的环境影响

构建"生产-运输-使用-废弃处置"的外卖全产业链，通过大样本企业调研与外卖平台大数据分析，计算8个样本城市不同材质与规格的外卖餐盒、餐具、包装袋的市场使用比例，挖掘骑手配送的海量数据，收集城市垃圾处理处置情况，系统评估外卖全过程的环境影响.结果表明，外卖包装物全产业链中生产环节（45%）与废弃处置环节（50%）为环境影响的主要来源，严重程度依次为固废排放、水污染、资源能源消耗和大气污染.所在城市及选用包装物材质的不同，外卖行业造成的环境影响会有显著区别，全产业链上的各环节需相互配合，多主体共同承担环境责任，采取差别化的减缓应对措施.