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1.
典型土壤中除草剂甲基磺草酮降解特性研究   总被引:1,自引:0,他引:1  
农产品质量和安全是一项重要的民生问题,环境介质中农药的迁移、转化与降解行为已成为环境科学的重要议题。以除草剂甲基磺草酮为研究对象,进行了甲基磺草酮在3种典型土壤中的室内模拟降解试验和自然光照降解研究,以灭菌土壤为对照,详细分析了甲基磺草酮在土壤中降解和大自然光照降解的主要影响因素。结果表明,甲基磺草酮在3种供试土壤中的光照降解速率依次为宜兴水稻土淮南水稻土盐城盐碱土,其不灭菌降解半衰期分别为12.16、27.73、34.68 d,灭菌降解半衰期分别为38.51、86.64、138.63 d,光照半衰期为8.56、18.73、25.67 d,所有降解均遵循一级动力学方程。与灭菌对比,非灭菌土壤明显具有较快的降解速率,说明土壤中微生物是甲基磺草酮降解的重要影响因素之一;同时,自然光照对甲基磺草酮的降解有一定的促进作用。土壤理化性质一定程度上影响了土壤微生物活性和群落结构,最终影响除草剂在土壤中的降解行为。  相似文献   

2.
利用气相色谱仪建立了土壤中乙羧氟草醚残留量的分析检测方法,并在实验室条件下研究了其在河南潮土、吉林黑土、江西红壤中的降解动态,为其环境和生态安全性评价提供重要的科学依据。结果表明:①土壤中的乙羧氟草醚残留物用丙酮-乙酸乙酯(1∶2,V/V)混合液提取,经弗罗里硅土SPE柱净化,浓缩后用气相色谱仪(带63Ni-ECD)进行检测;当添加浓度为0.01、0.05、0.5mg.kg-1时,添加回收率为86.9%~98.3%,标准偏差为1.50%~9.99%,最低检出量为1×10-12g,最低检出浓度为0.01mg.kg-1。②乙羧氟草醚在3种不同类型的土壤中降解速率大小依次为河南潮土>吉林黑土>江西红壤,降解速率常数分别为9.92×10-2、6.42×10-2和2.89×10-2,降解半衰期分别为7.0、10.8和24.0h,符合一级动力学方程。土壤pH值对乙羧氟草醚的降解有显著影响,乙羧氟草醚在碱性土壤中降解较快,在酸性土壤中降解较慢。根据国内农药在土壤中的残留性划分标准,乙羧氟草醚为易降解农药。  相似文献   

3.
乙草胺在土壤环境中的降解及其影响因子的研究   总被引:19,自引:1,他引:19  
采用实验室模拟方法研究了乙草胺在不同土壤中的降解动态。结果表明,在未灭菌的土壤中,乙草胺3种添加浓度(1.25、2.5和5.0mg·kg-1)处理的半衰期为2.8~5.1d,远远小于在灭菌土壤中3种添加浓度处理的半衰期(20.0~25.1d);乙草胺在偏碱的华北褐土中降解较快,2.5mg·kg-1处理的半衰期为4.2d,而在偏酸的东北黑土和湖南红土中降解较慢,半衰期为6.5~10.7d;土壤相对含水量由13%增至27%,乙草胺降解半衰期由7.3d缩短至3.0d;随着环境温度增高(20℃上升至30℃),乙草胺降解速度加快(半衰期由5.7d缩短至3.3d);乙草胺在黑暗条件下降解半衰期为3.8d,而在光照条件下的半衰期为5.2~6.5d。可见,5种试验因子对土壤中乙草胺的降解均有不同程度的影响。其中土壤微生物是影响乙草胺降解的主要因素,有利于土壤中微生物生长的环境因素,如偏碱的土壤、较高的环境温度和土壤湿度等,对土壤中乙草胺的降解有促进作用。  相似文献   

4.
为预测和评价双氟磺草胺对水资源及土壤环境的潜在风险提供依据,采用室内模拟试验方法,研究双氟磺草胺在不同土壤(黑土、红壤和水稻土)环境中的降解、吸附、淋溶以及在土壤表面的挥发性和光解性等归趋特征。结果表明:双氟磺草胺在吉林黑土、云南红壤与贵州水稻土中的降解符合一级动力学方程,其在3种土壤中的降解半衰期分别为12.8d、15.0d和12.6d,属于易降解农药;双氟磺草胺在3种土壤中的吸附符合Freundlich方程,Kd值(吸附常数)分别为1.83、1.14和0.537,3种土壤中均难吸附。经土壤薄层层析试验,当溶剂展开18cm时,双氟磺草胺在吉林黑土、云南红壤与贵州水稻土中主要分布在12~18cm、9~18cm和9~18cm土层中,其Rf值(比移值)均为0.917,极易移动。双氟磺草胺在土壤表面光解遵循一级动力学方程,Ct=4.355 8e-0.002 t,光解半衰期为346.5h,属于难光解农药。在(25±2)℃,气体流速为500mL/min的条件下,双氟磺草胺在土壤表面的挥发速率小于0.04%,属于难挥发农药。双氟磺草胺在土壤中难挥发、难光解、难吸附、易移动,但其在土壤中降解较快,对土壤环境的风险性小。  相似文献   

5.
【目的】评价雷公藤生物碱在土壤中的环境行为,为推动该植物源杀虫剂的开发和应用提供依据。【方法】参照《化学农药环境安全评价试验准则》(中华人民共和国农业部),采用土壤吸附和土柱淋溶试验,研究雷公藤生物碱在3种土壤(东北黑土、河南二合土和关中土娄土)中的吸附性能;采用土壤降解试验,以灭菌和未灭菌的桃园、小麦田、甘蓝田土壤为研究对象,检测了雷公藤生物碱在不同土壤中的降解性能。【结果】雷公藤生物碱在东北黑土、河南二合土及关中土娄土上的吸附性能可以用Freundlich平衡方程进行拟合,其在以上3种土壤中的吸附常数Kd分别为15.21,8.62和11.05,均属较难吸附,也难淋溶。在未灭菌的桃园土壤、小麦田土壤及甘蓝田土壤中,雷公藤生物碱的降解半衰期分别为10.06,9.92和8.88d,均属易降解;而在灭菌的上述3种土壤中,雷公藤生物碱降解较慢,处理32d后的降解率分别为49.71%,30.82%和33.33%。【结论】雷公藤生物碱在土壤中难移动、降解快,对土壤环境较为安全。  相似文献   

6.
土壤中双氰胺降解及与降解菌的关系   总被引:1,自引:0,他引:1  
采用灭菌土培、非灭菌土培、田间蔬菜种植、添加外源降解菌土培试验研究了土壤中双氰胺(DCD)降解及与降解菌的关系.结果显示,不论是单施DCD、尿素配施DCD,还是碳酸氢铵配施DCD的土壤,灭菌处理的土壤中DCD半衰期分别比不灭菌处理的长13.56、5.79、14.51 d.降解菌生长期间,降解菌总量(x)与DCD降解呈显著正相关,拟合的线性方程为y=3.1841x-2.5452,r=0.9752.外源DCD降解真菌可在灭菌土壤中定殖并有效降解DCD,培养15d后,U+DCD+DCD降解菌处理土壤中DCD降解真菌的数量增加至36.40× 105 cfu,且DCD含量极显著降低.这些结果表明土壤中DCD降解与降解菌关系极为密切,添加外源真菌加速了土壤中DCD降解.  相似文献   

7.
通过不同浓度、灭菌和不灭菌处理,毒死蜱在油菜叶面上降解规律及其影响因子的研究,分析了施药浓度与叶面上毒死蜱的降解规律。结果表明:毒死蜱在油菜叶面的残留量均随着取样时间的增加而逐渐减少,且农药在施用初期降解较快,后期降解速率缓慢;其对应灭菌处理的半衰期均小于不灭菌处理的半衰期;不同施药浓度300×、600×和900×对叶面毒死蜱半衰期影响较大:农药浓度越高,其半衰期越短。  相似文献   

8.
双草醚对土壤呼吸作用及土壤酶活性的影响   总被引:3,自引:1,他引:3  
通过模拟试验研究了除草剂双草醚对土壤呼吸强度和土壤酶活性的影响。结果表明,双草醚施用初期刺激土壤呼吸作用但随后产生抑制作用,施用20d后,浓度愈大对土壤呼吸作用的抑制愈明显;双草醚轻微抑制土壤中过氧化氢酶活性,21d后基本恢复正常;双草醚对脲酶活性有刺激作用,且低浓度处理酶活性明显高于高浓度处理。统计分析结果表明双草醚属于低毒农药。  相似文献   

9.
采用室内模拟试验,研究植物杀虫活性成分杠柳新苷P在不同水体和不同类型土壤中的降解与移动特性,分析其对不同水体与不同类型土壤的污染风险性。结果表明:温度和pH对杠柳新苷P在水中的降解均有一定程度的影响。温度为50℃、pH=9时,降解速率最快,其水解半衰期为2.36d。土壤降解与土壤淋溶试验表明,杠柳新苷P在麦田土、果园土和菜园土中的降解半衰期分别为4.33、4.25和3.85d,降解速率依次为菜园土果园土麦田土;对比试验研究表明,在未灭菌的土壤中,杠柳新苷P的降解速率比灭菌的土壤中显著加快。  相似文献   

10.
为评价异恶唑草酮的环境安全性,采用室内模拟试验方法,研究了异恶唑草酮在不同环境介质(空气、水和土壤表面)的挥发特性,在不同质地土壤(潮土、水稻土、黑土和红壤土)的吸附特性,和2种水-沉积物系统中的降解特性。结果表明:异恶唑草酮在潮土、水稻土、黑土和红壤土中的吸附均符合弗罗因德利希(Freundlich)方程,吸附常数值分别为0.640 6、1.376 2、0.816 9和1.289 5,在土壤中属于难吸附农药。异恶唑草酮在湖泊(杭州西湖)水-沉积物系统和河流(杭州运河)水-沉积物系统中的好氧降解和厌氧降解均符合一级动力学方程,好氧降解半衰期分别为73.7 h和75.3 h,厌氧降解半衰期分别为42.3 h和43.0 h,在水-沉积物系统中属于易降解农药。在20~25 ℃、气体流速为500 mL·min-1的条件下,异恶唑草酮在空气、水和土壤表面的挥发率均小于1%,属于难挥发性农药。试验结果表明,异恶唑草酮在空气、水和土壤表面难挥发,在土壤中难吸附,在水-沉积物系统中降解快,环境风险较小。  相似文献   

11.
采用室内模拟实验方法,以太湖水稻土、江西红壤和东北黑土为代表性土壤,研究了噻虫啉等3种烟碱类杀虫剂在土壤中的降解、吸附特性,并利用GUS(Ground Ubiquity Score)指数分析了其对地下水污染的影响。结果表明,3种烟碱类杀虫剂在3种土壤中均较易降解,降解半衰期在5~31d之间,属于易降解农药,降解特性与土壤理化性质及农药本身性质有关。3种烟碱类杀虫剂在江西红壤、太湖水稻土与东北黑土中的吸附较好地符合Freundlich方程,Kd值在0.30~14.70之间,KOC在42.8~1750.9之间,属难吸附农药。吸附性强弱与农药本身溶解性和土壤有机质含量有关,水溶性越强吸附越弱,有机质含量越高,吸附性越强。3种烟碱类杀虫剂在太湖水稻土中的GUS值均小于1.8,而在江西红壤中,其GUS值均大于1.8,这3种杀虫剂在江西红壤中均有一定的淋溶性,对地下水均有一定的污染风险。  相似文献   

12.
采用室内培养法和土柱法,研究了2-羟基-1,4-萘醌在土壤中的降解作用和淋溶行为。结果表明,2-羟基-1,4-萘醌在灭菌和非灭菌土壤中的降解半衰期分别为3.47~6.98d和0.42~0.53d,且随着2-羟基-1,4-萘醌浓度增加,其降解半衰期延长。说明微生物对其降解过程起主导作用。参考POPs国际公约关于化学品持久性的定义,2-羟基-1,4-萘醌在土壤中属于易降解有机物。通过2-羟基-1,4-萘醌在土壤中的淋溶研究发现:当其添加浓度为5mg·kg-1和10mg·kg-1时,各处理土层中均未检出2-羟基-1,4-萘醌;当添加浓度为20mg·kg-1时,仅在0~10cm土层样品中检测到2-羟基-1,4-萘醌。与未老化土壤相比,2-羟基-1,4-萘醌在老化土壤中的淋溶作用减弱。  相似文献   

13.
苯醚甲环唑在土壤中的降解动力学及其影响因子   总被引:3,自引:1,他引:2  
研究了苯醚甲环唑在北京、萧县、杭州及长沙4个地区土壤中的降解动力学,并探讨了土壤微生物、温度、含水量及药剂质量分数对其降解的影响.结果表明:苯醚甲环唑在4个地区土壤中的降解半衰期为11.63~21.77 d.土壤微生物对苯醚甲环唑降解起主导作用,灭菌土壤降解半衰期是非灭菌条件下的6.09倍;15~40℃范围内,温度升高,土壤中苯醚甲环唑降解加快,15~25℃降解速率增加幅度较大;士壤含水量过高(150%)和过低(25%)都不利于苯醚甲环唑降解,而土壤中药剂质量分数的增大对苯醚甲环唑降解则起阻碍作用.  相似文献   

14.
The determination of the environmental fate of Bt insecticidal protein released by Bt rice plants in paddy soils is a key issue in its ecological risk assessment. In this study, the impacts of soil water content, pH, and temperature on the degradation of Cry1Ab protein expressed in the leaves of Bt rice KMD2 were studied in the laboratory. Three types of paddy soils were used, i.e., blue clayey paddy soil, pale paddy soil on quaternary red soil, and marine-fluvigenic yellow loamy paddy soil. Ground powders of KMD2 leaf blades were mixed with each type of soil, and degradation dynamics of Cry1Ab were measured using enzyme-linked immunosorbent assay (ELISA). The degradation rate of Cry1Ab was high at the early experimental stage, but slowed down steadily at middle and later stages, which could be described by exponential equations, with the half-life period of degradation determined as 1.8-4.0 d. The soil water content, pH, and temperature could affect the degradation of Cry1Ab, but the effects of soil pH and temperature were relatively greater. In general,Cry 1 Ab degradations were slower under lower soil pH and temperature conditions, especially for marine-fluvigenic yellow loamy paddy soil.  相似文献   

15.
The determination of the environmental fate of Bt insecticidal protein released by Bt rice plants in paddy soils is a key issue in its ecological risk assessment. In this study, the impacts of soil water content, pH, and temperature on the degradation of CrylAb protein expressed in the leaves of Bt rice KMD2 were studied in the laboratory. Three types of paddy soils were used, i.e., blue clayey paddy soil, pale paddy soil on quaternary red soil, and marine-fluvigenic yellow loamy paddy soil. Ground powders of KMD2 leaf blades were mixed with each type of soil, and degradation dynamics of Cry lAb were measured using enzyme-linked immunosorbent assay (ELISA). The degradation rate of CrylAb was high at the early experimental stage, but slowed down steadily at middle and later stages, which could be described by exponential equations, with the half-life period of degradation determined as 1.8-4.0 d. The soil water content, pH, and temperature could affect the degradation of CrylAb, but the effects of soil pH and temperature were relatively greater. In general, CrylAb degradations were slower under lower soil pH and temperature conditions, especially for marine-fluvigenic yellow loamy paddy soil.  相似文献   

16.
影响Bt稻离体叶中Cry1Ab杀虫蛋白降解的环境因子研究   总被引:2,自引:0,他引:2  
 【目的】研究转Bt基因水稻表达的外源Bt杀虫蛋白在土壤中的环境去向,以便进行转BT基因水稻的生态风险性评价。【方法】室内采用ELISA法,研究了转Bt基因水稻克螟稻2号(KMD2)粉碎叶片中Cry1Ab杀虫蛋白在3种水稻土,即青紫泥田、黄筋泥田和黄松田土中不同土壤含水量、土壤pH值和温度条件下的降解动态。【结果】供试叶片粉中Cry1Ab蛋白在3种水稻土中的降解动态均可用一级化学反应动力学指数方程来拟合,降解半消减期t0.5为1.8~4.0 d。【结论】土壤含水量、pH和温度对Cry1Ab蛋白降解速率均有一定影响,但pH和温度的影响更为明显。通常pH较低的酸性土壤和低温不利于土壤中Cry1Ab蛋白的降解,特别是在酸性黄松田中降解最慢。  相似文献   

17.
储藏和加工方式对稻谷中毒死蜱和三唑磷残留量的影响   总被引:1,自引:0,他引:1  
[目的]了解稻谷加工方式和储藏方式对稻米中毒死蜱和三唑磷残留动态的影响机制。[方法]采用液相色谱-三重四极杆质谱法同时检测稻米中的毒死蜱及其代谢物3,5,6-三氯-2-吡啶酚(3,5,6-Trichloro-2-pyridinol,TCP)和三唑磷残留,分析碾磨、蒸煮、发芽加工以及储藏温度(37和4℃)对毒死蜱和三唑磷残留量的影响。[结果]毒死蜱及其代谢物TCP、三唑磷等农药残留多数分布在米糠层;短时间的蒸煮无法明显降低稻谷中毒死蜱的残留量;发芽稻谷中毒死蜱及其代谢物TCP、三唑磷的残留量显著低于未发芽稻谷;在37℃储藏条件下,毒死蜱的降解方程为C=0.899e~(-0.005t)(R~2=0.855 6),半衰期为138.6 d;三唑磷降解方程C=0.768e-0.009t(R~2=0.822 8),半衰期77.0 d,近似满足一级动力学模型方程;在4℃低温储藏条件下,稻谷中毒死蜱和三唑磷的残留量变化不大。[结论]碾磨和发芽加工有利于降低稻谷的农药残留量,低温储藏稻谷不利于残留农药的降解。研究可为稻米加工过程的风险评估以及开发稻米中农药残留的消解技术提供参考。  相似文献   

18.
通过田间试验,采用气相色谱法分析研究了溴虫腈在湖南和浙江两地稻田土壤、稻田水和水稻植株中的消解动态。结果表明:溴虫腈在水稻土壤、稻田水和水稻植株中的平均添加回收率分别为90.0%~108.0%、96.2%~105.0%和87.9%~105.0%;溴虫腈在稻田环境中的消解动态符合一级动力学指数模型,在两试验地稻田土壤中的平均半衰期为11.17 d;稻田水中的平均半衰期为5.17 d;水稻植株中的平均半衰期为6.27 d。  相似文献   

19.
按照“化学农药环境安全评价试验准则”的规定,研究了毒死蜱在土壤中的主要环境行为——吸附性、移动性、挥发性及降解的特性。结果表明,土壤具有较强的吸持毒死蜱农药的能力,吸附常数(Kd)为:壤土213.51,粘土182.82和砂土157.01;毒死蜱属于在壤土、砂土中不易移动,在粘土中不移动的农药品种;毒死蜱在壤土和粘土属难挥发,在砂土属中挥发;毒死蜱在壤土、粘土和砂土中的降解半衰期分别为23.9d、12.6d和9.8d,属于易土壤降解的农药品种。  相似文献   

20.
【Objective】 The straw degradation rate, microbial community structure changes and functional microbial community composition involved in straw decomposition in soils were researched, and the research results could provide the theoretical foundation for revealing microbial mechanism of the soil organic matter transformation and accumulation. 【Method】 Two typical subtropical paddy soil in China, including Changshu Wushan soil and Yingtan Red paddy soil, were collected as the research materials. We anaerobically incubated the soils with/without 13C-enriched rice straw for 38 days. Gaseous samples were regularly collected to investigate mineralization rate of straw in dynamic changes. The soil samples were collected to analyze the dynamic changes of the microbial community composition related to straw decomposition by using 13C-PLFA-SIP technology. 【Result】 At the early stage before day 12 of the anaerobic culture, straw degraded slowly, and straw had positive priming effect on soil organic matter (SOM). At the stage of day 12-18, straw degraded rapidly and then the rate tended to be slow after day 18. At the end of incubation, straw mineralization rate was 24% and 33% in Red paddy soil and Wushan soil, respectively. The contribution of straw C to C efflux increased with incubation time, which was 53%-60% and 54%-57% to CO2 and CH4 efflux, respectively. The microbial biomass and activity were improved in the soil with straw, and the microbial activity in Wushan soil was higher than that in Red paddy soil. During straw degradation, 16:0 (general bacteria) was the main groups. i16:0, i15:0 (G + bacteria) and 18:1ω9c (fungi) were also important microbial groups involved in straw degradation. The relative abundance of straw-derived gram-positive (G +) bacteria and actinomycetes increased and gram-positive (G -) bacteria decreased with incubation time. The proportions of straw-derived PLFAs were 27%-32% and 18%-24% in Red paddy soil and Wushan soil PLFAs, respectively. The straw utilization efficiency was higher in fungi and general bacteria, while G - bacterial and actinomycetes PLFAs were preferentially linked to extant soil organic matter (SOM) mineralization. The microbial community composition was different between Wushan soil and Red paddy soil with rice straw. The straw-derived microbial community composition was similar in two soils, but the SOM-derived microorganisms were differences. 【Conclusion】 The mineralization of straw C lagged behind extant SOM during anaerobic straw degradation. The microbial activity and diversity in soil were important factors influencing the efficiency of straw mineralization. After adding straw in soil, it’s showed differences from the microbial community composition, which were mainly involved in the differences between SOM-derived microorganisms, and SOM was an important factor leading to these differences.  相似文献   

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