百菌清(chlorothalonil)在水中的光化学降解

研究了光源种类、溶液pH、水温和表面活性剂对百菌清光解的影响.结果表明,百菌清水溶液在高压汞灯、紫外灯和太阳光照射下的光解半衰期分别为22.4、82.5和123.8 min;在太阳光和高压汞灯照射下,百菌清在碱性溶液中比中性和酸性溶液中光解快;随着水温的升高,百菌清光解速率加快,水温平均每升高10 ℃,光解速率大约增大1倍.表面活性剂十二烷基磺酸钠、Tween 60和Span 20对百菌清的光解表现出显著的光敏化效应,十六烷基三甲基溴化铵对百菌清光解有强烈的光猝灭效应.     

韭菜和土壤中毒死蜱的残留与降解动态

在大棚和露地栽培条件下,研究了不同浓度的毒死蜱灌根施药后土壤和韭菜中毒死蜱的残留与降解动态.结果表明:韭菜中毒死蜱的降解速度比土壤中快,平均半衰期分别为3.41 d和7.40 d;在大棚和露地栽培条件下,韭菜中毒死蜱的降解速率差异不大,平均降解半衰期分别为3.37和3.44 d.施药灌根后第21天,韭菜中毒死蜱的残留量(0.021 ～0.102mg·kg-1)基本低于GB 2763-2005规定的最大残留限量标准(≤0.1 mg·kg-1).新生韭菜中仍残留少量毒死蜱,但明显低于药后第一次刈割.土壤中残留的毒死蜱对韭菜中的农药残留量有显著影响.     

丁草胺在不同类型水中的光化学降解

研究了除草剂丁草胺在氙灯、高压汞灯光照下的光解动态。结果表明,丁草胺在氙灯光照作用下,其光解速率为纯水>河水>塘水>稻田水;丁草胺在氙灯光源下的光解速度比高压汞灯下低;其光解率与浓度(剂量)呈反相关;充N₂脱O₂使丁草胺的光解速度减缓。     

TMV在不同水体与温度条件下的灭活动力学

了解植物病毒在不同水体与温度条件下的灭活规律具有重要的理论与实际意义.本文以典型植物病毒烟草花叶病毒(TMV)为模型,比较了其在不同温度条件下,在闽江水、自来水、生活污水、微孔滤膜过滤除菌污水及超纯水中的灭活动力学.结果显示,温度是导致TMV灭活的重要因素,水温升高,病毒灭活速率加快;此外,某些水质因子也影响TMV的灭活效率,其中可溶性盐的存在及其含量对TMV的灭活会因所处的环境不同而异;某些微生物或代谢产物对植物病毒TMV具有灭活作用,而能生化降解的有机质加速TMV灭活可能是通过促进水体中的微生物增殖而起作用.     

维生素B12的光解研究及发酵液中维生素B12检测新方法的建立

采用HPLC检测法研究5,脱氧腺苷钴胺素和甲基基钴胺素的水溶液在不同光源及不同照度下的光解情况,结果表明随着光能量的增加光解速度加快。利用脱氧腺苷钴胺素的光解性质,探索了一种检测发酵液中维生素B12含量的新方法。将含有钴胺素的细胞破碎液完全光解后,测定光解后的产物羟基钴胺素,以此来确定维生素B12产量。此方法简便快速、重复性好,可应用于发酵生产维生素B12的各个环节。     

不同温度下毒死蜱和噻嗪酮对褐飞虱的毒力作用

为了明确温度对杀虫剂毒杀作用的影响,本文研究了5个温度梯度(22℃、25℃、28℃、31℃和34℃)下毒死蜱和噻嗪酮对褐飞虱的毒杀作用。结果表明毒死蜱在不同温度下对褐飞虱的毒力变化与噻嗪酮有所不同。处理时间相同时毒死蜱的LC50随温度升高而逐渐下降。毒死蜱处理24 h、72 h、120 h时,毒死蜱对褐飞虱的LC_(50)在22℃下分别的50.15、16.15和15.33 mg/L,而在34℃下分别降低为6.70、4.16和1.92 mg/L。在实验的5个温度下,噻嗪酮对褐飞虱的LC_(50)没有显著差异。同一温度下,噻嗪酮的LC50随处理时间的增加而降低,但没有显著差异。在全球变暖的大环境下,明确温度对毒死蜱和噻嗪酮的毒力影响状况,对于杀虫剂的合理使用具有一定的指导意义。     

枯草芽胞杆菌降解毒死蜱特性研究

研究生物量、pH、毒死蜱浓度和温度对枯草芽胞杆菌3374菌株(编号为GU086422)在水溶液中降解毒死蜱特性,考察该菌株对白菜上毒死蜱残留的降解特性。结果表明,在毒死蜱质量浓度为240 mg/L、pH7.0、温度30℃的适宜条件下,枯草芽胞杆菌3374菌株对毒死蜱的降解率达到92.48%。该菌株能够有效提高白菜叶面上毒死蜱残留的降解速度,表明其在白菜上具有有效降解毒死蜱的能力,在无公害农产品生产中具有广阔的应用潜力。     

山地草原生物量的垂直变化及其与气候变暖和施肥的关系

 试验将3种土壤(酸性棕壤、灰壤土、粘泥炭土)／植被的土柱从位于英格兰北部的Great Dun Fell(GDF)移入同一山体低海拔的Newton Rigg(NR),利用海拔高差造成的温差(4.2℃)模拟全球变暖对生物量的影响;和利用施肥(20kgNhm-2·a-1、10kgPhm-2·a-1)试验模拟全球变暖下,温度升高诱发土壤有机质分解速度加快,营养元素浓度升高对生物量的影响。结果表明：海拔变动造成的温度差异使生物量差异极显著(P≤0.01)。温度升高使粘泥炭土、酸性棕壤、灰壤土地上总生物量比对照分别提高51％、78％及66％;同时,物种组成大大改变,剪股颖在群落总生物量中所占的比例急剧升高。但不同施肥处理未使样品间生物量出现显著差异,从而得出结论：全球变暖引起的土壤有机质分解速度加快不会直接对生物量造成重要影响;而温度是影响生物量及物种组成变化的主要因素。     

TMV在不同水体与温度条件下的灭活动力学

了解植物病毒在不同水体与温度条件下的灭活规律具有重要的理论与实际意义。本文以典型植物病毒烟草花叶病毒(TMV)为模型,比较了其在不同温度条件下,在闽江水、自来水、生活污水、微孔滤膜过滤除菌污水及超纯水中的灭活动力学。结果显示,温度是导致TMV灭活的重要因素,水温升高,病毒灭活速率加快;此外,某些水质因子也影响TMV的灭活效率,其中可溶性盐的存在及其含量对TMV的灭活会因所处的环境不同而异;某些微生物或代谢产物对植物病毒TMV具有灭活作用,而能生化降解的有机质加速TMV灭活可能是通过促进水体中的微生物增殖而起作用。     

温度对土壤中外源氨基酸、多肽的矿化及其吸收动力学的影响

研究了不同温度（1 ℃、15 ℃和25 ℃）对3种园艺生产系统（有机生产系统OS、转换期生产系统TS、常规生产系统CS）土壤中外源添加氨基酸、多肽的矿化及其吸收动力学特性的影响.结果表明：随着温度的升高,外源添加的氨基酸和多肽在土壤中的矿化速度加快.在1 ℃、15 ℃和25 ℃下,3种供试土壤中谷氨酸（Glu）的平均半衰期分别为13.3、6.8和5.5 h;而谷氨酰 苯丙氨酸（Glu-Phe）的平均半衰期则分别为29.7、7.5和4.4 h.土壤的氨基酸、多肽的吸收动力学试验表明,土壤对氨基酸、多肽的吸收速率随着外源添加氨基酸和多肽浓度及温度的增加而提高.土壤对氨基酸的最大吸收速率(V_max)和亲和力（K_m）及对多肽的吸收速率（V_h）均随温度的升高而增大.在0～2.5 mmol·L^-1浓度范围内,土壤对氨基酸的吸收动力学曲线遵循经典的米氏动力学曲线,而多肽则表现为线性模式.3种园艺生产系统土壤的氨基酸和多肽的周转速率、吸收动力学参数（V_max、K_m和V_h）均表现为OS>TS>CS.总之,温度显著影响了氨基酸、多肽在土壤中的矿化及其吸收动力学特性.     

Products of the photolysis of 3,6-dichloropicolinic acid (the herbicide lontrel) in aqueous solutions

We studied the composition of products of the photochemical degradation of 3,6-dichloropicolinic acid (DCPA), the active principle of Lontrel, a herbicide broadly used in agriculture. Ultraviolet irradiation (mimicking the natural sunlight action) did not degrade DCPA completely to environmentally safe products. The rate of DCPA degradation was notably lower when distilled water was replaced by river water and even lower in sea water. Chromatomass spectrometry revealed 9 compounds among the photolysis products, in addition to undegraded DCPA.     

Products of the photolysis of 3,6-dichloropicolinic acid (the herbicide lontrel) in aqueous solutions

We studied the composition of products of the photochemical degradation of 3,6-dichloropicolinic acid (DCPA), the active principle of Lontrel, a herbicide broadly used in agriculture. Ultraviolet irradiation (mimicking the natural sunlight action) did not degrade DCPA completely to environmentally safe products. The rate of DCPA degradation was notably lower when distilled water was replaced by river water and even lower in sea water. Chromatomass spectrometry revealed 9 compounds among the photolysis products, in addition to undegraded DCPA.     

Sequential degradation of <Emphasis Type="Italic">p</Emphasis>-cresol by photochemical and biological methods

Sequential photo-and biodegradation of p-cresol was studied using a mercury lamp, as well as KrCl and XeCl excilamps. Preirradiation of p-cresol at a concentration of 10^?4 M did not affect the rate of its subsequent biodegradation. An increase in the concentration of p-cresol to 10^?3 M and in the duration preliminary UV irradiation inhibited subsequent biodegradation. Biodegradation of p-cresol was accompanied by the formation of a product with a fluorescence maximum at 365 nm (λ_ex = 280 nm), and photodegradation yielded a compound fluorescing at 400 nm (λ_ex = 330 nm). Sequential UV and biodegradation led to the appearance of bands in the fluorescence spectra that were ascribed to p-cresol and its photolysis products. It was shown that sequential use of biological and photochemical degradation results in degradation of not only the initial toxicant but also the metabolites formed during its biodegradation.     

Optimization of Chlorpyrifos Degradation by Assembled Bacterial Consortium Using Response Surface Methodology

Chlorpyrifos is a commonly used organophosphate pesticide. Its extensive use and associated serious soil and water contamination have gained increasing environmental concern. Biodegradation is a promising way to remediate chlorpyrifos contamination. There are many reports on various chlorpyrifos degrading microorganisms, but only a few on biodegradation of chlorpyrifos by consortia. Hence, the present study attempted to assemble a novel bacterial consortium C5 for the biodegradation of chlorpyrifos. The 16S rRNA gene-based molecular analysis revealed that the bacterial consortium consisted of Staphylococcus warneri CPI 2, Pseudomonas putida CPI 9 and Stenotrophomonas maltophilia CPI 15. Optimization of chlorpyrifos degradation by the consortium C5, using a Box–Behnken design, was carried out taking into account four important variables: temperature, pH, the initial concentration of chlorpyrifos and time of incubation. C5 is capable of giving 90% degradation of chlorpyrifos (125 ppm) in 8 days of incubation under optimized conditions of pH (7) and temperature (30°C). Growth curve and degradation study under optimized conditions confirmed that consortium could improve the biodegradation potential. From these results, we conclude that the novel consortium C5 of three species can be used to eliminate chlorpyrifos from various environmental compartments and can be implemented in bioreactors in a cost-effective, safe and environmentally friendly manner.     

水杨酸对高温强光胁迫下小麦叶绿体D1蛋白磷酸化及光系统Ⅱ功能的影响

为了研究水杨酸（SA）对高温强光胁迫下小麦叶片类囊体膜D₁蛋白磷酸化和PSⅡ功能的影响,用0.5 mmol·L^-1 SA溶液预处理灌浆期小麦叶片,以水预处理为对照,然后将预处理植株进行高温强光（35 ℃,1 600 μmol·m^-2·s^-1）处理,测定胁迫处理过程中小麦旗叶光合电子传递速率、净光合速率、叶绿素荧光参数及D₁蛋白的变化.结果表明：SA预处理有效抑制了高温强光下D₁蛋白的净降解,保持了较高的D₁蛋白磷酸化水平、全链电子传递速率和PSⅡ电子传递速率,维持了较高的PSⅡ原初光化学效率（F_v/F_m）、实际光化学效率(Ф_PSⅡ)、光化学淬灭系数（q_P）和净光合速率（P_n）.表明外源SA通过调节小麦叶绿体D₁蛋白的周转,减轻了高温强光胁迫对叶片光合机构的损伤,有利于PSⅡ的正常运转.     

水杨酸对高温强光胁迫下小麦叶绿体D1蛋白磷酸化及光系统Ⅱ功能的影响

为了研究水杨酸（SA）对高温强光胁迫下小麦叶片类囊体膜D₁蛋白磷酸化和PSⅡ功能的影响,用0.5 mmol·L^-1 SA溶液预处理灌浆期小麦叶片,以水预处理为对照,然后将预处理植株进行高温强光（35 ℃,1 600 μmol·m^-2·s^-1）处理,测定胁迫处理过程中小麦旗叶光合电子传递速率、净光合速率、叶绿素荧光参数及D₁蛋白的变化.结果表明：SA预处理有效抑制了高温强光下D₁蛋白的净降解,保持了较高的D₁蛋白磷酸化水平、全链电子传递速率和PSⅡ电子传递速率,维持了较高的PSⅡ原初光化学效率（F_v/F_m）、实际光化学效率(Ф_PSⅡ)、光化学淬灭系数（q_P）和净光合速率（P_n）.表明外源SA通过调节小麦叶绿体D₁蛋白的周转,减轻了高温强光胁迫对叶片光合机构的损伤,有利于PSⅡ的正常运转.     

Sequential degradation of p-cresol by photochemical and biological methods

Sequential photo- and biodegradation of p-cresol was studied using a mercury lamp, as well as KrCl and XeCl excilamps. Preirradiation of p-cresol at a concentration of 10(-4) M did not affect the rate of its subsequent biodegradation. An increase in the concentration of p-cresol to 10(-3) M and in the duration preliminary UV irradiation inhibited subsequent biodegradation. Biodegradation of p-cresol was accompanied by the formation of a product with a fluorescence maximum at 365 nm (lambdaex 280 nm), and photodegradation yielded a compound fluorescing at 400 nm (lambdaex 330 nm). Sequential UV and biodegradation led to the appearance of bands in the fluorescence spectra that were ascribed to p-cresol and its photolysis products. It was shown that sequential use of biological and photochemical degradation results in degradation of not only the initial toxicant but also the metabolites formed during its biodegradation.     

The Comparative Photodegradation Activities of Pentachlorophenol (PCP) and Polychlorinated Biphenyls (PCBs) Using UV Alone and TiO2-Derived Photocatalysts in Methanol Soil Washing Solution

Photochemical treatment is increasingly being applied to remedy environmental problems. TiO₂-derived catalysts are efficiently and widely used in photodegradation applications. The efficiency of various photochemical treatments, namely, the use of UV irradiation without catalyst or with TiO₂/graphene-TiO₂ photodegradation methods was determined by comparing the photodegadation of two main types of hydrophobic chlorinated aromatic pollutants, namely, pentachlorophenol (PCP) and polychlorinated biphenyls (PCBs). Results show that photodegradation in methanol solution under pure UV irradiation was more efficient than that with either one of the catalysts tested, contrary to previous results in which photodegradation rates were enhanced using TiO₂-derived catalysts. The effects of various factors, such as UV light illumination, addition of methanol to the solution, catalyst dosage, and the pH of the reaction mixture, were examined. The degradation pathway was deduced. The photochemical treatment in methanol soil washing solution did not benefit from the use of the catalysts tested. Pure UV irradiation was sufficient for the dechlorination and degradation of the PCP and PCBs.