太湖西部河湖氮污染物来源及转化途径分析

通过2014年枯水、丰水两期监测,综合分析了太湖西部入湖河流与湖区水体及其沉积物的无机氮形态与同位素特征,并利用δ~(15)N识别了太湖西部上游区氮污染来源及转化途径的生物化学作用机制.结果表明:NO_3~--N与NH_4~+-N为研究区域入湖河流无机氮的主要形态,而NO_3~--N为西部湖区水体无机氮的主要形态;δ~(15)N-NO_3~-的数值范围揭示了西部入湖河流在枯水季NO_3~--N主要来源于农用化肥,有少量矿化土壤有机氮,而丰水季则以生活污水为主,有少量矿化土壤有机氮及农用化肥;δ~(15)N-NH_4~+的数值范围说明了生活污水是河流水体NH_4~+-N的主要来源;通过水体及沉积物样品NO_3~--N、NH_4~+-N、δ~(15)N-NO_3~-、δ~(15)N-NH_4~+的协同分析可知,湖区氮的赋存形态主要受湖区水体硝化作用及沉积物内反硝化作用的影响.     

多级强化地下水修复技术对NH_4~+-N的去除机制

为解决地下水污染修复技术中PT(抽出处理)和PRB(渗透性反应墙)存在的一些不足,搭建了MET(多级强化地下水修复技术)小试装置,以NH4+-N为目标污染物,研究MET对地下水中NH4+-N的去除效果及机制.结果表明,在进水水力负荷为14.68 m3/(m2·d)、ρ(NH4+-N)为25.0 mg/L的条件下,装置连续运行45 d,NH4+-N去除率呈先降后升、平稳后再下降的趋势,平均值达90%以上.出水ρ(NH4+-N)平均值为2.0 mg/L,其中,硝化作用和微生物同化作用使ρ(NH4+-N)平均下降13.9和5.2mg/L,分别占进水ρ(NH4+-N)的54%和20%;植物作用、基质永久吸附作用和挥发作用分别使ρ(NH4+-N)下降2.9、0.7和0.7mg/L,占进水ρ(NH4+-N)的12%、3%和3%.综上,MET对地下水中NH4+-N的去除率可达90%,实现了高效去除NH4+-N的目标.     

生活污水回用作循环冷却水补充水处理方案的研究

分析了自来水及经膜生物反应器处理后的生活污水的水质指标，计算了水质判断指数，结果表明两者均为腐蚀性水质。通过静态缓蚀实验筛选合理的药剂，结果表明HEDP，ATMP，PBTCA的最高缓蚀率均高达90％以匕，HEDP，PBTCA与Zn^2＋复配的协同效果较好，复配后最高缓蚀率提高到98％以上。研究了考虑阻垢问题时的水处理药剂配方，通过正交试验筛选出最佳药剂浓度配方为：T-325：PBTCA：Zn^2＋=8：4：3。     

滇东主要断裂带温泉CO_2成因浅析

通过对滇东主要断裂带上典型温泉的地质背景、环境条件、水化学及碳、氦稳定同位素分析,探讨这些温泉CO2释放的一般规律。分析表明滇东主要断裂带温泉具有特殊的碳来源,其CO2释放与沿小江断裂混杂第三纪煤层(褐煤)有关。     

微型反应柱在含铬废水处理试验研究中的应用

针对镀铬车间废水,采用活性炭吸附处理法对Cr6 和Cr3 的去除效果进行了系统的试验.通过微型反应柱集成装置对穿透时间、吸附容量及活性炭再生方法进行了研究,动态试验表明该装置能有效地处理含铬废水.     

A~2/O法应用于酒店污水处理工程的实例

某酒店污水处理工程设计规模 80 0m3 d ,进水CODCr2 50～ 30 0mg L ,BOD51 50～ 1 0 0mg L ,SS 1 4 0～ 1 2 0mg L ,氨氮2 5mg L ,动植物油 50mg L。采用处理工艺 ,2年来的运行效果显示 ,出水水质稳定达到广东省《水污染物排放限值》(DB4 4 2 6 2 0 0 1 )第二时段第一级标准。     

天津地区人群对六六六的暴露分析

以天津地区六六六(HCH)各介质浓度的实测数据和文献中相关参数为基础资料 ,采用多介质暴露模型,估算了天津地区人群对环境中HCH的暴露水平 .计算结果说明 ,该地区人群的终身日均暴露量为0.05μg·(kg·d)^-1,儿童、青少年和成人亚群的暴露水平分别为 0.10、0.06和0.04 μg·(kg·d)^-1.膳食摄入占总暴露量的 87%以上 ,是最主要的途径 ;其次是呼吸暴露 ,对总暴露的贡献达5%～10%.各项参数中,膳食结构和食品、气相HCH残留水平是影响暴露的重要因素 .     

Adsorption of Pb, Cd to Fe, Mn oxides in natural freshwater surface coatings developed in different seasons

Metal oxides( Fe, Mn oxides) in natural surface coatings(biofilms and associated minerals) are believed to play a significant role n the fate and transport of trace metal in aquatic environments. Seasonal variation of Fe, Mn oxides and organic materials in surface oatings, which were developed periodically on glass slides in Nanhu Lake, Jilin Province, China over the time frame of three seasons,was investigated in order to understand the influence of metal oxides on Pb and Cd adsorption to heterogeneous surface coating materials(biofilm). Pb and Cd adsorption was measured under controlled laboratory conditions( mineral salts solution with defined speciation, ionic trength 0.05 mol/L, 25~C and pH 6.0). The classical Langmuir adsorption isotherm was applied to estimate equilibrium coefficients of Pb nd Cd adsorption to the surface coatings. In general, components in the surface coatings varied greatly with seasons altering and btained higher concentrations in summer while the content of iron oxides always exceeded that of manganese oxides. Correlation nalyses between the maximum adsorption of Pb and Cd and components in the surface coatings developed periodically indicated that Pb hase association with Mn oxides and Cd phase association with Fe oxides as well as Mn oxides were statistically significant. Effect of Mn xides on Cd adsorption was confirmed in view of its higher content in the surface coatings. The importance of ferromanganese oxides for b and Cd adsorption to the natural surface coatings developed in different seasons was evidenced.     

Purification and molecular weight distribution of a key exopolysaccharide component of Bacillus megaterium TF10

Extracellular polymeric substances (EPS) are organic metabolic compounds excreted by microorganisms. They largely impact microbial aggregate structures and functions. Extracellular polysaccharides (EP) in EPS are responsible for the formation of microbial aggregates. In this work, we successfully separated and characterized EP from EPS of the bacterium Bacillus megaterium TF10. Extraction of EP from EPS was optimized using Sevag''s reagent. Chemical characteristics, functional groups, and molecular weight (MW) distribu-tion of EP were compared with the harvested EPS and soluble microbial products (SMP). We found that the polymers of lower MW and free proteins were successfully removed by Sevag''s reagent. The higher MW components of EPS were predominantly polysaccharides, while the polymers of lower MW tended to secrete to the supernatant and were described as SMP. A part of the proteins in the EP was polysaccharide-bonded. Our results can be further used in elucidating the complex flocculation mechanisms in which EP play a major role.