溴氰虫酰胺及其代谢物在辣椒和土壤中的残留降解研究

建立了超高效液相色谱-串联质谱法(UPLC-MS/MS)测定辣椒和土壤中溴氰虫酰胺及其代谢物(J9Z38)残留量的方法,研究了溴氰虫酰胺和J9Z38在辣椒和土壤上的降解特性。样品经乙腈提取后用C18固相萃取柱净化,采用梯度洗脱程序、BEH C18色谱分离柱、应用UPLC-MS/MS正离子扫描测定溴氰虫酰胺和J9Z38。进行了添加浓度为0.01、0.10和1.00 mg/kg的回收实验,溴氰虫酰胺和J9Z38在辣椒和土壤中的日内平均回收率为88.6%~105.7%,日内相对标准偏差为3.8%~15.1%;日间平均回收率为91.4%~105.3%,日间相对标准偏差为4.9%~12.3%。溴氰虫酰胺和J9Z38在2.0~128.0μg/L浓度范围内相关系数r>0.9992,定量限分别为0.1和0.2μg/kg。应用本方法检测了田间实验样品,结果表明,溴氰虫酰胺在辣椒和土壤中降解半衰期分别为9.2~11.2 d和9.2~20.8 d,J9Z38在辣椒中残留量低于定量限,在土壤中降解半衰期为9.4 d;随着降水量增加,溴氰虫酰胺降解速度加快。     

UPLC-MS/MS法同时测定土壤中3种磺酰脲类除草剂残留

建立了QuEChERS法–超高效液相色谱–串联质谱法(UPLC-MS/MS)快速测定土壤中噻吩磺隆、苯磺隆、氯嘧磺隆3种磺酰脲类除草剂的方法。采用振荡提取、QuEChERS法净化方法处理土壤样品,利用UPLC-MS/MS分析,在多反应监测(MRM)模式下以0.1%甲酸水和乙腈为流动相梯度洗脱。3种除草剂在0.5~500μg/L的质量浓度范围内线性关系良好,相关系数为:0.996~0.999。在10,50μg/kg水平下进行加标回收实验,平均回收率为81.4%~92.9%,RSD为5.5%~10.6%,方法检出限(S/N=3)为0.12~0.16μg/kg。方法可用于大量实际土壤样品中3种除草剂的检测。     

凝胶渗透色谱-分散固相萃取法同时测定鸡蛋中多溴联苯醚及其衍生物、四溴双酚A和六溴环十二烷

建立了一种同时检测鸡蛋中四溴双酚A(TBBP A)、六溴环十二烷(HBCD)和多溴联苯醚(PBDEs)及其衍生物羟基多溴联苯醚(OH-PBDEs)和甲氧基多溴联苯醚(MeO-PBDEs)的凝胶渗透色谱(GPC)-分散固相萃取(DSPE)-液相色谱-串联质谱(HPLC-MS/MS)和气相色谱-负化学源质谱(GC-NCI/MS)的检测方法。样品经正己烷、二氯甲烷(1∶1,V/V)加速溶剂萃取,凝胶渗透色谱净化后,经100 mg十八烷基键合硅胶(C18)分散固相萃取吸附剂去除杂质,液相色谱-串联质谱和气相色谱-负化学源质谱方法测定,外标法定量。在蛋白和蛋黄样品中添加1.0或5.0μg/kg的目标物,其回收率分别为64.5%~97.2%和65.6%~109.2%(除BDE-85为54.8%,OH-BDE-137为47.4%外),相对标准偏差小于20.2%,定量限为0.01~0.2μg/kg。     

超高效液相色谱-串联质谱法同时测定水和沉积物中磺胺类、喹诺酮类和氯霉素类抗生素残留

建立了超高效液相色谱-串联质谱法(UPLC-MS/MS)同时测定水及沉积物中磺胺类、喹诺酮类和氯霉素类抗生素残留。水样前处理采用固相萃取,沉积物样品前处理采用加速溶剂萃取。该方法在9min内可完成目标化合物的UPLC-MS/MS分离分析。对于水和沉积物,20种目标化合物的检出限(S/N≥3)分别介于0.01~0.50ng/L和0.005~0.2μg/kg之间,在各自考察的浓度范围内线性关系良好(r≥0.995)。采用该方法测定了苏州地区地表水,共检出10种抗生素,浓度范围为0.79~240ng/L;测定底泥样品,共检出11种抗生素,浓度范围为0.37~27.0μg/kg。     

超高压液相色谱串联质谱法测定小油菜中3种农药残留

建立了小油菜中阿维菌素、氯虫苯甲酰胺和苯醚甲环唑3种农药残留的超高效液相色谱-串联质谱检测方法。样品经乙腈提取,SPE氨基固相萃取柱净化,超高效液相色谱-串联质谱(UPLC-MS/MS)同时进行检测。3种农药在小油菜样品中均存在程度不同的基质效应,因此,采用空白基质匹配的校准曲线外标法定量。3种农药均在0.5~500μg/L范围内具有良好的线性关系,相关系数均大于0.9996。在0.02~0.2 mg/kg范围内,平均添加回收率为84.0%~110.0%,相对标准偏差为1.2%~1.5%。阿维菌素、氯虫苯甲酰胺和苯醚甲环唑的检出限(LOD)分别为1.87,0.0115和0.0110μg/kg,定量限(LOQ)分别为6.24,0.0384和0.0366μg/kg。     

超高压液相色谱串联质谱法测定小油菜中3种农药残留EI北大核心CSCD

建立了小油菜中阿维菌素、氯虫苯甲酰胺和苯醚甲环唑3种农药残留的超高效液相色谱-串联质谱检测方法。样品经乙腈提取,SPE氨基固相萃取柱净化,超高效液相色谱-串联质谱(UPLC-MS/MS)同时进行检测。3种农药在小油菜样品中均存在程度不同的基质效应,因此,采用空白基质匹配的校准曲线外标法定量。3种农药均在0.5~500μg/L范围内具有良好的线性关系,相关系数均大于0.9996。在0.02~0.2 mg/kg范围内,平均添加回收率为84.0%~110.0%,相对标准偏差为1.2%~1.5%。阿维菌素、氯虫苯甲酰胺和苯醚甲环唑的检出限(LOD)分别为1.87,0.0115和0.0110μg/kg,定量限(LOQ)分别为6.24,0.0384和0.0366μg/kg。     

基于QuEChERS-液相色谱-串联质谱法测定稻米中嘧草醚和双草醚残留

采用改良的QuEChERS-液相色谱-串联质谱(LC-MS/MS)技术,建立了稻米中嘧草醚和双草醚残留量的检测方法。样品经酸化乙腈提取,由十八烷基键合硅胶(C18)吸附剂净化。以0.1%(体积分数)甲酸水(含5 mmol/L乙酸铵)-乙腈为流动相进行梯度洗脱,经ZORBAX SB C18色谱柱实现目标化合物的基线分离。采用电喷雾正离子(ESI+)模式扫描,动态多反应监测(dynamic MRM)技术定性分析,外标法定量。结果表明:在稻米基质中,嘧草醚和双草醚在各自的线性范围内线性关系良好(r2≥0.996);嘧草醚和双草醚的检出限(LOD)分别为0.8和3μg/kg。在3个添加水平下,嘧草醚和双草醚的平均回收率分别为76.6%~85.6%和73.0%~86.7%,相对标准偏差(RSD)分别为0.9%~3.4%和1.2%~5.5%(n=6)。该方法简便、快速、灵敏,适用于稻米中嘧草醚和双草醚的同时分析。     

QuEChERS-液相色谱-串联质谱法同时检测土壤和柑橘中吡唑醚菌酯、甲基硫菌灵及其代谢物多菌灵的残留

建立了QuEChERS-液相色谱-串联质谱法(LC-MS/MS)检测土壤和柑橘中吡唑醚菌酯、甲基硫菌灵及其代谢物多菌灵的分析方法。样品经甲醇或乙腈提取,N-丙基乙二胺(PSA)净化后,用液相色谱分离,电喷雾正离子多反应监测(MRM)模式进行质谱测定,以基质匹配标准溶液进行外标法定量。吡唑醚菌酯、甲基硫菌灵和多菌灵的定量限(LOQ,S/N=10)分别为5.8~7.0μg/kg、9.3~14.1μg/kg和2.1~2.6μg/kg。样品的加标回收率为75.48%~109.18%,相对标准偏差(RSD)为0.60%~5.11%(n=5)。该法快速简便,定量准确,用基质配制标准溶液能够有效、准确地校正LC-MS/MS测定吡唑醚菌酯、甲基硫菌灵和多菌灵残留的基质效应,满足土壤、橘皮、橘肉和柑橘全果实际样品的检测需求。     

气相色谱-质谱法同时测定土壤中的4种丙烯酸酯类农药

建立快速溶剂萃取-气相色谱质谱联用法同时测定土壤中的4种丙烯酸酯类(嘧菌酯,嘧菌胺,苯氧菌胺,醚菌酯)残留量的分析方法。将随机采集到的土壤样品自然风干,粉碎过筛。称取过筛后的样品5 g,置于萃取池中,以丙酮-乙酸乙酯(体积比为1∶1)作为萃取溶剂,于加速溶剂萃取仪中进行提取,收集提取液,氮吹至近干,用丙酮定容至1 mL,以0.45μm滤膜过滤后,上GC-MS/MS仪分析,色谱峰面积外标法定量检测。4种丙烯酸酯类的质量浓度在0.05~5.0μg/mL范围内与其色谱峰面积呈良好的线性关系,检出限为0.006~0.010 mg/kg,加标回收率为91.4%~94.6%,测定结果的相对标准偏差为2.48%~4.29%(n=6)。该方法前处理简单,定性及定量结果准确,适用于土壤中丙烯酸酯类残留的监测。     

超高效液相色谱-串联质谱法测定猪肉中硝基呋喃类代谢物

建立了超高效液相色谱-串联质谱(UPLC-MS/MS)测定猪肉组织中4种硝基呋喃类代谢物的分析方法.样品经盐酸水解,2-硝基苯甲醛衍生,乙酸乙酯提取净化,在正离子模式下以电喷雾电离串联质谱进行测定,内标法定量.在优化的实验条件下,4种代谢物在0.5~50μg/kg范围内线性良好,相关系数大于0.995,方法检出限为0.2μg/kg,定量限为0.5μg/kg.在0.5、1.0和10.0μg/kg的添加水平下,4种代谢物的平均回收率在74.6%~104.8%之间,相对标准偏差(RSD,n=6)在2.4%~15.6%之间.方法可应用于猪肉中4种硝基呋喃类药物代谢物残留的同时检测.     

QuEChERS/超高效液相色谱-串联质谱法测定土壤中31种磺酰脲类除草剂残留

建立了一种基于QuEChERS前处理技术和超高效液相色谱-串联质谱(UHPLC-MS/MS)同时测定土壤中31种磺酰脲类除草剂残留的方法。通过对色谱条件、提取溶剂、净化剂等进行优化,确定以甲醇和0.1%甲酸+5 mmol/L乙酸铵为流动相,1%(体积分数)乙酸-乙腈为提取溶剂,C18(25.00 mg/mL)为净化剂。31种磺酰脲类除草剂的线性关系良好,相关系数(r2)均不小于0.998 0,定量下限(S/N=10)为0.012~2.321μg/kg。3个加标水平(10、100、400μg/kg)下的平均回收率为71.8%~119%,相对标准偏差(RSD)为0.62%~13%。除烟嘧磺隆、三氟啶磺隆钠、玉嘧磺隆、啶嘧磺隆、氯吡嘧磺隆为中等强度基质效应外,其余待测物均表现为弱基质效应。该方法简便易操作,具有较好的灵敏度和准确度,适用于土壤中31种磺酰脲类除草剂残留的同时检测。     

超高效液相色谱-串联质谱法快速测定沉积物中11种藻毒素

建立了超高效液相色谱-串联质谱(UPLC-MS/MS)快速测定沉积物中11种藻毒素的方法。沉积物经冷冻干燥、粉碎过筛,用0.1 mol/L EDTA-Na4P2O7溶液涡旋超声提取,经HLB固相萃取小柱净化后,用甲醇-0.2%甲酸洗脱、浓缩并氮吹定容至1 m L。经Waters BEH C18色谱小柱,以乙腈-0.2%甲酸水溶液为流动相,梯度洗脱分离后,在电喷雾正离子模式下,以超高效液相色谱-串联质谱多级监测模式(MRM)外标法进行定性定量分析。结果表明:沉积物中11种藻毒素的检出限为1.0~5.0 ng/kg。对同一环境样品进行了0.1、1.0、4.0μg/kg不同水平的加标回收试验,平均回收率为70.3%~112.5%,相对标准偏差(RSD)为2.2%~9.3%。该方法快速、灵敏、准确,可应用于沉积物中11种藻毒素的快速监测。     

Degradation of imazosulfuron in different soils-HPLC determination

Imazosulfuron, 1-(2-chloroimidazo [1,2-a] pyridin-3-ylsulfonyl)-3-(4,6-dimethoxypyrimidin-2-yl)urea, is a new sulfonylurea herbicide applied once per growing season. It is highly active at low application levels and is used to control most annual and perennial broad-leaf weeds and some grasses in cereal crop. In this work the degradation of imazosulfuron in four different soils was investigated under aerobic laboratory conditions to evaluate its environmental fate. Test soils were treated with this herbicide in acetonitrile to obtain a final concentration of 0.2 mg kg(-1) (100 g ha(-1)), extracted with methylene chloride and analyzed by reversed-phase liquid chromatography (RP-HPLC) using a C(18) column coupled with UV detection. Recoveries of spiked soils ranged from 84.3 to 99.8% (RDS 0.0-4.9%; n = 4). The limits of quantitation ranged from 0.002 to 0.004 mg kg(-1). Imazosulfuron half-life, t(1/2), was calculated in each of the investigated soil. In aerobic conditions it ranged between 1 and 50 days.     

超高效液相色谱-串联质谱法分析鸡蛋中利巴韦林及其代谢物残留

建立了超高效液相色谱-串联质谱法同时快速测定鸡蛋中利巴韦林及其两种主要代谢物 TCONH2和RTCOOH 的分析检测方法。样品采用乙腈-水(9∶1, V/ V)提取,乙腈饱和正己烷除脂,C18结合 GCB 进行固相分散萃取除杂,Agilent ZORBAX SB-Aq 色谱柱(100 mm ×3.0 mm,1.8μm)分离,超高效液相色谱-串联质谱测定。结果表明：利巴韦林、TCONH2和 RTCOOH 分别在2.0~200μg/ L,0.5~200μg/ L,5.0~200μg/ L 浓度范围内,线性良好,相关系数 R2>0.99,检出限分别为0.54,0.09和1.54μg/ L,定量限分别为1.79,0.31和5.13μg/ L。在5.0,10.0和50.0μg/ L 加标水平下,利巴韦林和 RTCOOH 回收率分别为96.1%~99.6%和42.9%~58.3%;在0.5,2.0和5.0μg/ L 加标水平下,TCONH2的回收率为75.9%~106.7%,相对标准偏差均为4.2%~12.7%。实际样品测定结果表明,本方法操作简单、快速、准确,能够满足鸡蛋中利巴韦林及其两种主要代谢物的分析检测。     

Degradation and metabolism of imazapyr in soils under aerobic and anaerobic conditions

The degradation of imazapyr in four soils was investigated under laboratory aerobic and anaerobic conditions. Under aerobic conditions, imazapyr degraded faster in yellow–red soil than in other soils, and its persistence decreased depending on soil pH in the order coastal soil (pH 8.8)?>?silt-loamy paddy soil (pH 7.9)?>?fluvio-marine yellow loamy soil (pH 7.1)?>?Yellow–red soil (pH 5.3). However, soil pH did not affect imazapyr degradation under anaerobic conditions. The half-lives of imazapyr in soils under aerobic conditions were in the range of 26–44 days estimated by the first-order kinetics model, while 3–10 days calculated by two-stage model under anaerobic conditions. The preceding results demonstrated that anaerobic conditions contributed to imazapyr disappearance in soils. Based on the spectral data of APCI-MS, ¹H NMR and IR, structures of the following metabolites: 2,3-pyridinedicarboxamide, 2,3-pyridinedicarboxylic anhydride and 2,3-pyridinedicarboximide for aerobic treatments; 2,3-pyridinedicarboxylic anhydride and 2-(4-hydroxy-5-oxo-2-imdazolin-2-yl) nicotinic acid for anaerobic treatments, were identified. Degradation mechanism under the different conditions was also discussed.     

Bioremediation of Single and Mixture of Pesticide-Contaminated Soils by Mixed Pesticide-Enriched Cultures

In the present study, degradation efficiencies for individual as well as mixed pesticide in different Indian soils, by mixed pesticide-enriched cultures, were evaluated under submerged and unsaturated conditions, Lindane (L), methyl parathion (MP), carbofuran (C), and a mixture of L, MP, and C were used in the study. For all the various conditions considered, methyl parathion degradation was the maximum and lindane degradation was the minimum. The degradation kinetics of the pesticides in sandy, clayey, compost, and red soils by various microbial isolates were studied. It was observed that adsorption was maximum and degradation of pesticides was minimum in compost soil. The degradation efficiencies of pesticides in liquid phase associated with soil sediment were less than those under the normal liquid phase conditions as leaching of pesticides from soil phase was continuous. Pesticide degradation was more in submerged soils compared to that in unsaturated soils. The degradation by-products of individual and mixed pesticides in liquid, unsaturated, and submerged soils were identified. Different metabolites were produced under submerged and unsaturated conditions.     

分散固相萃取/超高效液相色谱-串联质谱法测定玉米和土壤中噻酮磺隆-异唑草酮及其代谢物残留

建立了分散固相萃取结合超高效液相色谱-串联质谱快速检测玉米和土壤中噻酮磺隆、异嚼唑草酮及其代谢物RPA203328与RPA202248残留的分析方法.样品经1％甲酸-乙腈溶剂提取,氯化钠盐析后,提取液经分散固相萃取净化,超高效液相色谱-串联质谱仪检测.考察了提取溶剂及吸附剂种类对分析结果的影响,优化了液相色谱-质谱条件,评估了优化实验条件下的方法性能.结果表明:在玉米样品中,4种分析物的基质效应均大于10％;在土壤样品中,除RPA202248基质效应小于10％外,其余3种分析物的基质效应均大于10％.噻酮磺隆、异唑草酮及其代谢物在0.001 ～ 1.0 μg/mL范围内线性关系良好,相关系数为0.994 5 ～0.999 5.加标浓度在0.005 ～0.1 mg/kg范围内的回收率为72.9％～ 116.5％,相对标准偏差(n=5)为0.75％ ～ 17.8％,定量下限为0.005 ～0.01 mg/kg.该方法前处理简单,分析时间短,准确度和灵敏度高,适用于玉米和土壤中噻酮磺隆、异唑草酮及其代谢物残留的快速检测.     

多次溶剂萃取-气相色谱/串联质谱法测定热熔胶中的多环芳烃

建立了热熔胶中16种多环芳烃( PAHs)的多次溶剂萃取-气相色谱/串联质谱测定方法。详细研究了样品的萃取条件、净化条件和气相色谱/串联质谱测定条件,并与气相色谱-质谱法进行了对比。样品以10 mL正己烷为萃取溶剂,于60℃超声萃取20 min,萃取液依次经冷冻后离心、二甲基亚砜萃取2次、正己烷反萃取2次进行净化,得到的净化液以气相色谱/串联质谱法多反应监测( MRM)模式进行检测。本方法的线性相关系数( R2)均大于0.9969,检出限为1.0~10μg/kg,精密度小于6.3%,16种PAHs的加标回收率为80.4%~117.6%。考察了串联质谱检测的基质效应,发现基质效应不明显。本方法检出限优于气相色谱-质谱法(23~94μg/kg),并能增加定性和定量分析的准确性。本方法灵敏、准确可靠,满足热熔胶中PAHs测试要求。     

超高效液相色谱-串联质谱法测定牛奶和奶粉中残留的左旋咪唑

建立了一种专属、灵敏的超高效液相色谱-串联质谱(UPLC-MS/MS)测定牛奶和奶粉中左旋咪唑残留量的方法。在碱性环境下用乙酸乙酯超声波提取试样中的左旋咪唑,再经稀盐酸反提取、强阳离子交换(SCX)固相萃取柱净化,采用BEHC18超高效液相色谱柱、乙腈-0.1%甲酸(体积比为15∶85)流动相分离,以电喷雾离子源正离子检测方式进行质谱分析。实验结果表明,在2.0～100.0 μg/L浓度范围内左旋咪唑呈良好的线性关系,其相关系数r=0.997。在低、中、高3个浓度添加水平下,左旋咪唑的回收率为64.5%～102.0%,相对标准偏差小于13.1%。牛奶中左旋咪唑检出限为0.4 μg/kg,奶粉中左旋咪唑检出限为2.0 μg/kg。