广州城市污泥中重金属的存在特征及其农用生态风险评价

分析了广州7种城市污泥中Zn、Cu、Pb、Cr、Mn、Ni的含量,研究了其中5种污泥中重金属的形态特征,并利用地累积指数（Igeo）和潜在生态危害指数法（RI）对污泥农用过程中重金属的潜在生态风险进行了综合性评价. 结果表明,广州不同来源城市污泥中Cu、Zn、Mn、Ni含量较高,变化幅度较大,而Pb、Cr含量较低. 除一种污泥中Cu超标外,其他重金属基本符合国家农用控制标准（GB18918-2002）,但所有污泥中重金属含量都超过珠江三角洲耕地土壤均值.不同重金属在不同污泥中的形态分布差异较大. 其中,含工业污水污泥中Cu、Cr还原态占很大的比例,Pb、Fe主要以还原态和残渣态存在;生活污水污泥中重金属主要以可氧化态和残渣态存在,酸可交换态中Mn的比例较高,易还原态中Zn的比例较高;5种污泥中Cu、Zn、Mn潜在迁移性最强.Igeo和RI评价结果表明,污泥中Cu、Zn、Mn是潜在的强生态风险元素,污泥在农用过程中具有一定生态风险性. Igeo和RI用于污泥农用过程中重金属的生态风险评价是可行的,与其它评价方法相比较, RI能更好地反映污泥中重金属对生态环境的综合影响.     

济源市平原区农田重金属污染特征及综合风险评估

铅锌冶炼区农田重金属污染问题受到广泛关注.本研究通过区域调查和空间分析明确济源市东部平原区农田土壤-小麦重金属污染特征,应用富集因子、潜在生态风险指数法和Monte Carlo模拟方法评估区域土壤重金属生态风险以及小麦Cd和Pb健康风险.结果表明：土壤Cd、Pb、Cu和Zn平均含量分别为1.51、97.1、29.0和79.5 mg·kg^-1,均高于河南省土壤元素背景值.其中74.2%和10.8%的样点Cd、Pb含量分别超过农田土壤风险筛选值,61.3%和40.9%的样点小麦Cd、Pb含量分别超过国家食品安全限量标准.富集因子研究结果表明土壤Cd污染程度最高.高风险区主要分布在西南部、西北部和中东部以铅锌冶炼为主的工业区.健康风险评估结果显示研究区小麦Cd非致癌风险和致癌风险高于国际推荐安全值的概率分别高达27.5%和100%.济源市小麦田Cd、Pb累积显著,需引起当地有关部门足够关注.空间分析与风险评价结果相结合,可以有效辨识高风险区域,进而为研究区污染防治和管控提供理论依据.     

典型行业再利用土壤重金属含量分布、来源解析及生态风险评价

为深入探究典型行业再利用土壤重金属污染特征及生态风险状况,基于上海市嘉定区49个地块315个不同深度剖面土壤样品数据,采用地累积指数和潜在生态风险指数评估Cd、Pb、Cu、Zn、Ni、Hg和As这7种重金属含量特征和潜在生态风险程度,并利用源解析受体模型（APCS-MLR）和正定矩阵因子分解模型（PMF）解析其污染来源.结果表明：①研究区土壤中除As外,其余重金属均不同程度超过上海市土壤背景值,表层土壤中Cd、Pb、Cu、Zn、Ni和Hg含量分别是背景值的3.54、2.34、2.91、1.20、3.75和4.40倍;7种重金属含量随着土壤垂直剖面深度的增加逐渐降低,重金属在表层土壤中存在一定程度的富集,人类活动影响了重金属在土壤中的分布规律.②研究区内APCS-MLR和PMF两种受体模型均识别出土壤重金属4种主要来源,源1（Cu、Zn和Pb）为金属制品和汽车制造混合源,源2（Ni和Cd）为电镀企业来源,源3（Hg）主要为化工企业来源,源4（As）为自然源,两种受体模型结合运用,进一步提高源解析的精准度和可信度.③地累积指数由大到小表现为：Hg（1.54）>Ni（1.32）>Cd（1.21）>Cu（0.96）>Pb（0.64）>Zn（-0.33）>As（-1.02）;潜在生态风险指数结果显示,研究区综合潜在生态风险指数RI值在32.50~4 910.97,均值为321.40,整体呈现较强潜在生态风险,再开发利用工业场地土壤中重金属Hg、Ni和Cd的污染值得进一步关注.     

河流水环境质量评价研究——对评价系统、评价方法的新探讨

本文旨在对河流水环境资源中水质、水量二要素的评价以及对定量、定性数据的综合评价进行方法论上的探讨。文中提出了模糊数学评价的改进方法,建立了一套水量评价标准和评价方法;建立了“优势度”概念并提出了水质、水量多目标定量、定性数据综合评价方法。以四川省沱江为例,对上述方法进行验证,根据评价结果划分河段,并对各河段的水资源合理利用及水环境规划提出建议。     

Adsorption of Cr(Ⅲ) from acidic solutions by crop straw derived biochars

Cr（Ⅲ） adsorption by biochars generated from peanut, soybean, canola and rice straws is investigated with batch methods. Adsorption of Cr（Ⅲ） increased as pH rose from 2.5 to 5.0. Adsorption of Cr（Ⅲ） led to peak position shifts in the FFIR-PAS spectra of the biochars and made zeta potential values less negative, suggesting the formation of surface complexes between Cr^3＋ and functional groups on the biochars. The adsorption capacity of Cr（Ⅲ） followed the order： peanut straw char 〉 soybean straw char 〉 canola straw char 〉 rice straw char, which was consistent with the content of acidic functional groups on the biochars. The increase in Cr^3＋ hydrolysis as the pH rose was one of the main reasons for the increased adsorption of Cr（Ⅲ） by the biochars at higher pH values. Cr（llI） can be adsorbed by the biochars through electrostatic attraction between negative surfaces and Cr^3＋, but the relative contribution of electrostatic adsorption was less than 5%. Therefore, Cr（Ⅲ） was mainly adsorbed by the biochars through specific adsorption. The Langumir and Freundlich equations fitted the adsorption isotherms well and can therefore be used to describe the adsorption behavior of Cr（Ⅲ） by the crop straw biochars. The crop straw biochars have great adsorption capacities for Cr（Ⅲ） under acidic conditions and can be used as adsorbents to remove Cr（Ⅲ） from acidic wastewaters.     

Effects of seed aerosols on the growth of secondary organic aerosols from the photooxidation of toluene

Hydroxyl radical （.OH）-initiated photooxidation reaction of toluene was carried out in a self-made smog chamber. Four individual seed aerosols such as ammonium sulfate, ammonium nitrate, sodium silicate and calcium chloride, were introduced into the chamber to assess their influence on the growth of secondary organic aerosols （SOA）. It was found that the low concentration of seed aerosols might lead to high concentration of SOA particles. Seed aerosols would promote rates of SOA formation at the start of the reaction and inhibit its formation rate with prolonging the reaction time. In the case of ca. 9000 pt/cm^3 seed aerosol load, the addition of sodium silicate induced a same effect on the SOA formation as ammonium nitrate. The influence of the four individual seed aerosols on the generation of SOA decreased in the order of calcium chloride〉sodium silicate and ammonium nitrate〉ammonium sulfate.     

伺服系统加速可靠性增长试验应用与探讨

加速可靠性增长试验是可靠性试验新的研究方向和应用领域,对于可靠性要求高、任务时间长、产品子样少或价格昂贵的航天产品的可靠性增长和评价工作有良好的实施效果.对加速可靠性增长试验技术的基本原理、应用和实施的必要性、加速应力选取方法和注意事项进行了阐述,结合某型伺服系统加速可靠性增长试验方案设计实例,对传统可靠性增长试验方案...     

Se(Ⅳ)和Se(Ⅵ)对小白菜生长及生理效应的影响

用盆栽试验研究了不同含量Se(Ⅳ)和Se(Ⅵ)对小白菜生长和生理效应的影响.结果表明,不同含量Se(Ⅳ)和Se(Ⅵ)对小白菜体生长和生理代谢的影响不尽相同.低含量硒（Se(Ⅳ)<10.0 mg·kg-1、Se(Ⅵ)<5.0 mg·kg-1）能够促进小白菜的生长,使其根变粗, 诱导脯氨酸的产生,阻止丙二醛（MDA）的合成,增强白菜的抗逆性,使其生物量明显提高;高含量硒会抑制小白菜的生长,导致植物体内脯氨酸合成下降,MDA含量增加,叶及根系生长受到抑制,地上和地下部干重显著急速下降（p<0.01）.小白菜根长、叶面积等生长指标均随Se(Ⅳ)和Se(Ⅵ)含量的增大而显著下降（p<0.01）;抑制小白菜根系生长的Se(Ⅳ)含量为60 mg·kg-1,明显高于Se(Ⅵ)含量（20.0 mg·kg-1）.相同硒含量下,Se(Ⅳ)处理的小白菜地上部干重为Se(Ⅵ)的1.1~3.0倍,说明本试验条件下Se(Ⅵ)的生物有效性和毒性均大于Se(Ⅳ).Se(Ⅵ)处理小白菜地上部分的硒含量显著高于地下部分,而Se(Ⅳ)处理小白菜地下部分的硒含量显著高于地上部分,小白菜地上和地下部分对Se(Ⅵ)的吸收量均显著高于Se(Ⅳ).综合生长和生理因子分析表明,地上部分生物量是反映Se(Ⅳ)及Se(Ⅵ)处理土壤上小白菜生长状况的理想指标.     

Low-carbon transition of iron and steel industry in China: Carbon intensity, economic growth and policy intervention

As the biggest iron and steel producer in the world and one of the highest CO₂ emission sectors, China's iron and steel industry is undergoing a low-carbon transition accompanied by remarkable technological progress and investment adjustment, in response to the macroeconomic climate and policy intervention. Many drivers of the CO₂ emissions of the iron and steel industry have been explored, but the relationships between CO₂ abatement, investment and technological expenditure, and their connections with the economic growth and governmental policies in China, have not been conjointly and empirically examined. We proposed a concise conceptual model and an econometric model to investigate this crucial question. The results of regression, Granger causality test and impulse response analysis indicated that technological expenditure can significantly reduce CO₂ emissions, and that investment expansion showed a negative impact on CO₂ emission reduction. It was also argued with empirical evidence that a good economic situation favored CO₂ abatement in China's iron and steel industry, while achieving CO₂ emission reduction in this industrial sector did not necessarily threaten economic growth. This shed light on the dispute over balancing emission cutting and economic growth. Regarding the policy aspects, the year 2000 was found to be an important turning point for policy evolution and the development of the iron and steel industry in China. The subsequent command and control policies had a significant, positive effect on CO₂ abatement.     

Control of aliphatic halogenated DBP precursors with multiple drinking water treatment processes: Formation potential and integrated toxicity

The comprehensive control efficiency for the formation potentials(FPs) of a range of regulated and unregulated halogenated disinfection by-products(DBPs)(including carbonaceous DBPs(C-DBPs), nitrogenous DBPs(N-DBPs), and iodinated DBPs(I-DBPs)) with the multiple drinking water treatment processes, including pre-ozonation, conventional treatment(coagulation–sedimentation, pre-sand filtration), ozone-biological activated carbon(O_3-BAC) advanced treatment, and post-sand filtration, was investigated. The potential toxic risks of DBPs by combing their FPs and toxicity values were also evaluated.The results showed that the multiple drinking water treatment processes had superior performance in removing organic/inorganic precursors and reducing the formation of a range of halogenated DBPs. Therein, ozonation significantly removed bromide and iodide,and thus reduced the formation of brominated and iodinated DBPs. The removal of organic carbon and nitrogen precursors by the conventional treatment processes was substantially improved by O_3-BAC advanced treatment, and thus prevented the formation of chlorinated C-DBPs and N-DBPs. However, BAC filtration leads to the increased formation of brominated C-DBPs and N-DBPs due to the increase of bromide/DOC and bromide/DON.After the whole multiple treatment processes, the rank order for integrated toxic risk values caused by these halogenated DBPs was haloacetonitriles(HANs)》haloacetamides(HAMs) haloacetic acids(HAAs) trihalomethanes(THMs) halonitromethanes(HNMs) 》I-DBPs(I-HAMs and I-THMs). I-DBPs failed to cause high integrated toxic risk because of their very low FPs. The significant higher integrated toxic risk value caused by HANs than other halogenated DBPs cannot be ignored.