DMPP对稻田田面水氮素转化及流失潜能的影响

采用杭嘉湖地区典型的小粉土和青紫泥土壤,进行水稻盆栽试验,研究新型硝化抑制剂3,4-二甲基吡唑磷酸盐(DMPP)对稻田田面水氮素转化及径流流失潜能的影响.结果表明,小粉土和青紫泥土壤稻田应用添加DMPP抑制剂的尿素,与常规尿素处理相比,田面水中铵态氮的浓度增加24.8%和16.7%,硝态氮浓度降低47.7%和70.9%,亚硝态氮浓度降低90.6%和88.9%,总无机氮浓度下降13.5%与23.1%,能显著减轻农田氮素流失对水环境存在的污染;DMPP可使田面水的电导率下降,降低盐基离子随农田排水或暴雨径流所导致的流失风险,有助于保护河流水体等地表水环境.     

饮用原水中微量NH_3-N的生物膜脱除

针对NH3-N浓度为1mg.l-1的饮用原水,分别以硅锰砂石和聚胺脂海绵作为硝化生物膜载体,考察了自制固定床生物膜反应器的脱氨效果.30d的连续运行结果表明,砂石载体系统达到95%—100%的NH3-N去除率,出水NH3-N浓度接近0,出水NO2--N浓度在0—0.02mg.l-1之间;而海绵载体系统虽然挂膜快,但运行阶段NH3-N去除率仅为10%—35%,出水NH3-N不能达标,且具有生物可降解性,反硝化过程优先导致NO2--N的积累.进一步考察了硅锰砂石生物膜系统稳定运行的最优参数,得出试验条件下,水力停留时间为6min,气水比为1:1,反冲洗周期为6d.硅锰砂石因其良好的孔隙率、粒径分布和密度等物理特性,以及化学稳定性和生物安全性,是含低浓度NH3-N原水生物膜净化的良好载体选择.     

生石灰对福寿螺的毒性效应研究

通过室内毒性试验,探索了生石灰对不同大小福寿螺的毒性效应。试验中将福寿螺按照壳高（H）分为小螺（5 mm≤H〈15 mm）、中螺（15 mm≤H〈25 mm）、大螺（25 mm≤H〈35 mm）和超大螺（35 mm≤H〈45 mm）,结果表明：（1）生石灰的控螺效应显著,尤其是对中小福寿螺具很强的抑制和杀灭作用;生石灰处理6 d,除了最低质量浓度0.05 g.L-1处理造成35%死亡率,其他处理死亡率均在70%以上,其中0.20、0.50、1.00和2.00 g.L-1处理中超过90%的福寿螺死亡。（2）生石灰对不同大小福寿螺的半抑制质量浓度（24 h）大小顺序为超大螺〉中螺、大螺〉小螺,半致死质量浓度（24 h）大小顺序为超大螺〉大螺〉中螺〉小螺;（3）生石灰对福寿螺的毒性以抑制效应为主,生石灰对福寿螺的平均半抑制质量浓度为0.06～0.22 g.L-1,低于平均半致死质量浓度0.11～1.09 g.L-1;（4）0.50 g.L-1和2.00 g.L-1质量浓度的石灰处理12 h后,福寿螺鰓组织SOD酶活性呈极显著下降,分别为对照的33%和38%。研究表明,生石灰可用于防治入侵生物福寿螺,在实践中可部分替代杀螺剂的使用。     

不同耕作方式下土壤氮素矿化和硝化特征研究

为探讨长期定位试验田不同耕作方式下土壤氮素矿化和硝化特征,采用室内恒温通气培养法,保持土壤田间持水量在65％条件下,测定不同耕作方式下表层土壤（0～20cm）在不同温度下的NH4^＋和NO3^-含量,并计算氮素矿化量和硝化率。结果表明,随着温度的升高,土壤氮素矿化和硝化作用均增强,几种耕作方式下土壤氮素矿化和硝化作用均表现为35℃〉30℃〉25℃。保护性耕作与水旱轮作和常规平作之间的矿化量存在显著的差异,垄作免耕〉厢作免耕〉水旱轮作〉常规平作。土壤氮素最终硝化率达到了60％～80％,表现为常规平作最高,水旱轮作次之,厢作免耕最低。矿化率与土壤有机质、碱解氮和速效磷对数均成显著正相关,相关系数分别为r^2=0．99,r^2=0．97,r^2=0．96,pH是影响硝化作用的重要因素,硝化率与土壤pH成显著正相关,r^2=0．991。     

基于发光细菌的细颗粒物(PM_(2.5))可溶性提取液综合生物效应测试方法及其应用

为科学评估PM_(2.5)对生物体综合生物效应,研究建立了利用费氏弧菌检测PM_(2.5)水溶性提取液的毒性测试方法,确立了PM_(2.5)样品提取液发光细菌毒性测试实验质量控制办法。对春节烟花爆竹燃放和沙尘污染过程的PM_(2.5)实样测试表明:烟花爆竹燃放期间的PM_(2.5)样品提取液发光抑制率值与微量金属元素等有毒有害组分浓度显著相关;沙尘污染期间的PM_(2.5)样本提取液中地壳元素浓度和发光抑制率值显著不相关。     

同步硝化反硝化过程中污染物的去除及温室气体的释放

采用缺氧-好氧SBR反应器,研究了同步硝化反硝化(SND)工艺污水生物脱氮过程中污染物去除效果和温室气体(N2O,CH4和CO2)的释放情况.结果表明,与顺序式硝化反硝化工艺(SQND)的总氮去除率63.78%相比,SND大大地提高了总氮的去除,去除率达90.39%.同时,SND过程刺激了温室气体的释放,其温室气体释放总量为SQND的4.5倍.SND反应器N2O每周期释放量为34.28 mg,且主要集中于曝气阶段.而SQND过程N2O释放量仅为6.89mg,为SND过程的1/5.SND过程和SQND过程,每周期CO2的释放量分别为493.52,320.28mg.两反应器中CH4的释放量都很低,接近于零.     

不同硝化负荷MBR去除类固醇雌激素的研究

以雌酮(E1)和17α-乙炔基雌二醇(EE2)2种典型类固醇雌激素为研究对象,考察了不同硝化负荷好氧MBR对其的去除特性.结果表明,硝化负荷为6.19,0.35,10.58mg/(gMLSS·d)的MBR对E1平均去除率分别为72.33%、64.06%和71.77%,去除负荷分别为29.98,23.06,27.66mg/(gMLSS·d);对EE2平均去除率分别为55.40%、42.87%和58.90%,去除负荷分别为22.39,16.54,23.58mg/(gMLSS·d).E1去除效果均优于EE2.MBR硝化负荷与氨氧化细菌之间有较好的线性关系;而SEs去除负荷与氨氧化细菌及硝化负荷之间不满足线性关系.硝化负荷为0.35mg/(gMLSS·d)时,SEs去除负荷较低,硝化负荷达到6.19mg/(gMLSS·d)时,SEs的去除负荷显著提高,而当硝化负荷增加到10.58mg/(gMLSS·d)时,SEs去除负荷不再有效提高.     

氯酚类化合物对紫背浮萍生长及叶绿素含量的影响

以我国本土水生植物紫背浮萍为受试物种,利用其生长抑制和叶绿素含量的变化评价了3种氯酚类化合物的毒性效应.结果显示:2,4-二氯酚(2,4-DCP), 2,4,6-三氯酚(2,4,6-TCP)和五氯酚(PCP)对紫背浮萍的96h IC50值分别为12.73,8.49,1.12mg/L.根据化学物质对水生生物毒性分级标准,3种物质均为高毒.2,4-DCP,2,4,6-TCP和PCP对紫背浮萍基于叶绿素含量变化的最大可接受浓度(MATC)分别为2.24,1.58, 0.35mg/L,对应的急慢性毒性比(ACR)分别为5.68,5.37和3.20.     

Influence of some parameters on adsorption rate and toxicity of cadmium in activated sludge

The influence of pH, competitor ions (NaNO₃) and aerobic and anaerobic stabilization of activated sludge on the cadmium uptake by activated sludge solids was investigated. Above 0.08 mg L^‐1 cadmium in solution, biosorption was found to follow the Freundlich isotherm. Active cellular uptake of soluble cadmium does not appear to be a significant mechanism of the biosorption. In addition, the cadmium uptake is not completely reversible. The adsorption of cadmium by activated sludge seems to involve a physico‐chemical mechanism with especially weak electrostatic interactions with ion‐exchange reaction. The optimum adsorption pH was 7.5. Adsorption is influenced by sodium ion concentrations up to an equivalent conductivity of 10 000 μS cm^‐1. Aerobic and anaerobic stabilization of activated sludge increase systematically the initial adsorption capacities. Respirometric measurements were done to evaluate the inhibitive effects of cadmium on activated sludge. Monod's equation and the equation of non‐competitive inhibition were used to describe the toxicity related to cadmium uptake. These two equations appear to be complementary.     

Effect of dietary factors and environmental chemicals on intestinal drug metabolizing enzymes

The liver is the major site of metabolism of foreign chemicals, but contribution from intestinal biotransformation can influence the overall disposition of chemicals. The intestinal drug‐metabolizing enzymes are located in the endoplasmic reticulum and they possess biochemical properties similar to those of the hepatic system. In general, the rate of in vitro metabolism of drug substrates in intestines is lower than in the liver. There seem to be differences in regulation and induction of hepatic and intestinal drug‐metabolizing enzymes. The in vitro intestinal metabolism of foreign chemicals is affected by several factors including the nutritional status of the animal. Dietary components such as vitamins, lipids and vegetables can modify the activities of intestinal drug‐metabolizing enzymes. Phenobarbital or 3‐methyl‐cholanthrene (3‐MC) pre‐treatment induces the hepatic metabolism of a wide variety of drug substrates in a number of species, while the stimulation of intestinal enzymes is both substrate and species specific. Rabbit intestinal drug‐metabolizing enzymes seem to be resistant to induction by foreign chemicals.