舟山本岛河流沉积物重金属污染特征与评价

测试和研究了舟山本岛8条河流沉积物中Cu、Zn、Pb、Cd、Hg、As、Cr的含量与分布特征,利用地累积指数法和Hakanson潜在生态风险指数法对沉积物重金属进行了生态风险评价,结果表明:(1)基于地累积指数法的评价表明Hg、Cr、As为清洁,Cu、Pb、Cd、Zn为轻度污染;(2)基于单项潜在生态风险系数的评价表明研究区内沉积物中Cu、Pb、As、Zn、Cr处于轻微等级,Cd和Hg则有不同程度的污染;该区域重金属生态风险等级顺序为Cd>Hg>Cu>Pb>As>Cr>Zn;(3)根据综合潜在生态风险指数,城关河和展茅河处于中等风险等级。     

中亚地区气候生产潜力时空变化特征

根据中亚5 国100 个气象站1901-2000 年月平均温度和降水资料,运用Miami、Thornthwaite Memorial 模型对中亚地区气候生产潜力进行了计算,用气候倾向率、Mann-Kendall 法、并结合ArcGIS 和SPSS 对其时空变化特征及驱动力进行了分析。结果表明：①中亚地区100 a 降水气候生产潜力（Yr）和蒸散气候生产潜力（Ye）均呈逐渐增加的趋势,温度气候生产潜力（Yt）趋势相反,Yr 和Ye 均发生了4 次突变,Yt 没有发生突变;②气候生产潜力区域差异明显,其中,Yt 呈从西南向东北减少的趋势,Yr 和Ye 变化比较复杂,大致具有东部大于西部的规律;③增温增湿的气候变化趋势有利于中亚气候生产潜力的提高,中亚气候生产潜力对增湿的响应更敏感。     

海五联区域阴极安全保护智能监测系统

阐述了ACPS-Ⅱ阴极安全保护智能监测系统的组成、特点以及在海五联合站的应用,指出阴极安全保护监测技术是阴极安全保护技术的发展方向,有着广泛的推广应用前景.     

安徽铜陵新桥河上游沉积物重金属污染及潜在生态风险评价

安徽铜陵新桥河的沉积物样中,重金属浓度为Cu〉Zn〉Pb〉Cr,按国家土壤环境二级质量标准评价,Cu、Zn含量已超标。其新桥河的沉积物样中,Cu、Zn的污染参数很高,含量为高风险或极高风险;Pb污染参数较高,含量为一般风险或高风险。同时新桥河的沉积物样中,Cu具有很高的潜在生态风险。     

Influence of flooding and metal immobilising soil amendments on availability of metals for willows and earthworms in calcareous dredged sediment-derived soils

Soil amendments previously shown to be effective in reducing metal bioavailability and/or mobility in calcareous metal-polluted soils were tested on a calcareous dredged sediment-derived soil with 26 mg Cd/kg dry soil, 2200 mg Cr/kg dry soil, 220 mg Pb/kg dry soil, and 3000 mg Zn/kg dry soil. The amendments were 5% modified aluminosilicate (AS), 10% w/w lignin, 1% w/w diammonium phosphate (DAP, (NH₄)₂HPO₄), 1% w/w MnO, and 5% w/w CaSO₄. In an additional treatment, the contaminated soil was submerged. Endpoints were metal uptake in Salix cinerea and Lumbricus terrestris, and effect on oxidation-reduction potential (ORP) in submerged soils. Results illustrated that the selected soil amendments were not effective in reducing ecological risk to vegetation or soil inhabiting invertebrates, as metal uptake in willows and earthworms did not significantly decrease following their application. Flooding the polluted soil resulted in metal uptake in S. cinerea comparable with concentrations for an uncontaminated soil.     

大沽排污河河口地区沉积物中重金属污染及其潜在生物毒性风险评价

本文以大沽排污河口表层沉积物为研究对象,分别运用ERL/ERM和生态危害指数两种评价方法对沉积物中6种重金属的潜在生物毒性风险进行评价,并对两种方法的评价结果进行对比。经均一化处理,重金属的含量均值由大到小的顺序排列为铬（168 mg/kg）〉锌（157 mg/kg）〉镍（60.7 mg/kg）〉铜（45.3 mg/kg）〉铅（7.31 mg/kg）〉镉（0.215 mg/kg）。经计算20个采样断面的沉积物中重金属毒性单位总和均在3~4之间,有80%的采样断面沉积物中重金属毒性单位总和大于3.5,毒性单位总和最大值为3.789。说明大沽排污河口沉积物中重金属的潜在生物毒性水平较低,可视为无生物毒性。     

会泽某铅锌矿周边农田土壤重金属生态风险评价

为了了解云南会泽某铅锌矿废周边农田土壤中重金属含量及潜在的生态危害程度,利用野外采样与实验室分析相结合的方法,以会泽某铅锌矿周边农田土壤（0-20 cm）为研究对象,分析其中7种的重金属（Cd、As、Pb、Cr、Cu、Zn和Hg）含量,并采用风险评价代码法和Hankanson潜在生态风险指数法评价对重金属污染程度与潜在生态风险进行评价。结果表明：7种重金属都存在超标或污染,其中Pb、As、Cd等的污染较为严重。统计学分析结果表明,Pb、As、Hg、Zn、Cd来源相同,铅锌矿冶炼污染物的排放可能是导致研究区域农田土壤重金属含量升高的主要原因。7种重金属化学形态也不尽相同：在重金属有效态中,Cd的水溶态和可提取态较高（平均值达到31.2%）;Pb、Cu和Zn可还原态、可氧化态这两部分含量较高,两部分之和的平均值分别可达到27.9%、30%和27.2%;Hg、As和Cr的残渣态含量较高,平均值分别为90.4%、72.9%和76.8%。风险评价代码评价结果表明,54.4%的样点Cd为高生态风险,45.6%的样点Cd为中度生态风险;100%的样点Zn为中度生态风险;Cu有41.2%的点位属于低生态风险,58.8%的点位属于中度生态风险;As和Pb主要以低生态风险为主（所占比例分别为92.6%和91.8%）;Hg主要以无生态风险为主（所占97.1%）。Hakanson潜在生态风险指数法结果表明,7种重金属潜在生态危害大小顺序为：Cd（331）〉Hg（127.5）〉Pb（43.6）〉As（14.9）〉Cu（9.3）〉Zn（2.3）〉Cr（2.1）。7种重金属的综合潜在生态风险指数（RI）的范围为58.2-1839.3。11%的采样点处于轻微生态风险程度,27.1%的采样点处于中等生态风险程度,46.3%的的采样点处于强生态风险程度,15.6%的采样点处于很强的生态风险程度。综上所述,该矿区周边农田土壤受到了严重的重金属污染,由此引起的重金属生态风险不容忽视?     

燃气热电系统火灾爆炸预先危险性分析

通过对燃气热电系统的工艺过程分析,识别出系统内潜在的7种火灾爆炸危险因素.运用预先危险性分析法对各类危险因素进行了具体分析,得出事故后果的危险等级为Ⅲ～Ⅳ级,存在严重的危害性,对此提出了相应的安全对策措施.     

Temporal Changes in Streamflow and Attribution of Changes to Climate and Landuse in Wisconsin Watersheds

Previous historic trends analyses on 21st Century hydrologic data in the United States generally focus on annual flow statistics and have continued to use USGS hydro‐climatic data network (HCDN) stations, although post‐1988 diversions and runoff regulations are not reflected in the HCDN. Using a more recent dataset, Geospatial Attributes of Gages for Evaluating Streamflow, version II (GAGES II), compiled by Falcone (2012), which includes more watersheds with reference conditions, a comprehensive analysis of changes in seasonal, and annual streamflow in Wisconsin watersheds is demonstrated. Given the pronounced influence of seasonal hydrology in Wisconsin watersheds, the objective of this study is to elucidate the nature of temporal (annual, seasonal, and monthly) changes in runoff. Considerable temporal and regional variability was found in annual and seasonal streamflow changes between the two historic periods 1951‐1980 and 1981‐2010 considered in the study. For example, the northern watersheds show relatively small changes in streamflow discharge ranging from ?6.0 to 4.2%, while the southern watersheds show relatively large increases in streamflow discharge ranging from 13.1 to 18.2%. To apportion streamflow changes to climate and nonclimatic factors, a method based on potential evapotranspiration changes is demonstrated. Results show that nonclimatic factors account for more than 60% of changes in annual runoff in Wisconsin watersheds considered in the study.     

Decomposition of 1,4-dioxane by vacuum ultraviolet irradiation: Study of economic feasibility and by-product formation

We report the first use of vacuum ultraviolet (VUV) treatment to decompose 1,4-dioxane, a persistent organic contaminant that is difficult to remove by conventional drinking water treatment processes. The efficiency of VUV treatment was compared to that of VUV- and UV-based advanced oxidation processes (AOPs) (VUV/TiO₂, VUV/H₂O₂, UV/TiO₂, and UV/H₂O₂), and by-product formation was investigated. VUV treatment decomposed 1,4-dioxane more rapidly than did UV and UV/TiO₂ treatments. The decomposition rate was enhanced when VUV irradiation was combined with TiO₂ or H₂O₂. VUV/H₂O₂ decomposed 1,4-dioxane more rapidly than UV/H₂O₂ at a low H₂O₂ dose (1 mg/L), but the rate difference became small at a high H₂O₂ dose (5 mg/L). Electrical energy per order analysis revealed that VUV treatment, and the VUV- and UV-based AOPs, were economically feasible for 1,4-dioxane decomposition. Using raw water samples, we investigated by-product formation during VUV treatment and the effect of VUV irradiation on chlorinated disinfection by-product formation potential. Although the samples contained high concentrations of bromide, no bromate was produced by VUV treatment. VUV treatment slightly decreased trihalomethane formation potential (THMFP), whereas haloacetic acid formation potential (HAAFP) was unchanged, and total aldehyde concentration increased. The trend in HAAFP agreed with that had been reported for the VUV irradiation with much higher dose (Buchanan et al., 2006), whereas the trend in THMFP was different from that with much higher dose. THMFP, HAAFP, and aldehyde concentration were reduced by subsequent treatment with granular activated carbon (GAC) or biological activated carbon (BAC). Nitrite was produced by VUV treatment but disappeared after subsequent BAC treatment. These results suggest that VUV treatment should be combined with GAC or BAC treatment to suppress by-product formation.