Trace level determination of selected sulfonylurea herbicides in wetland sediment by liquid chromatography electrospray tandem mass spectrometry

Sulfonylurea herbicides are widely used in crop production on the Canadian prairies and a portion of these herbicides applied to cropland are inevitably lost to surrounding aquatic ecosystems. Little is known regarding the presence of sulfonylurea herbicides in wetlands located amongst cropland. This paper describes a new analytical method for the extraction and the determination of seven sulfonylurea herbicides (thifensulfuron-methyl, tribenuron-methyl, ethametsulfuron-methyl, metsulfuron-methyl, rimsulfuron, nicosulfuron and sulfosulfuron) in wetland sediment. The method provided > 85% analyte recovery from fortified sediment for six of the seven sulfonylurea herbicides with a limit of quantification (LOQ) of 1.0 μ g kg^{? 1}. Tribenuron-methyl had significantly lower recovery compared to the other six sulfonylurea herbicides (LOQ = 2 μ g kg^{? 1}). Mean recovery standard deviations were < 10%. This methodology was used to quantify sulfonylurea herbicide residues in sediment samples collected from prairie wetlands situated within the agricultural landscape of Saskatchewan and Manitoba, Canada. This is the first-known detection of sulfonylurea herbicide residues in prairie wetland sediments. Ethametsulfuron-methyl, sulfosulfuron and metsulfuron-methyl, the three most environmentally persistent of the seven sulfonylurea herbicides monitored in the surveillance component of this study, were most frequently detected in wetland sediment with mean concentrations ranging from 1.2 to 10 μ g kg^{? 1}.     

Matrix effects in analysis of dialkyl phosphate metabolites of organophosphate pesticides in urine by gas chromatography/tandem mass spectrometer

Urinary dialkyl phosphate metabolites (DAPs) are used as biomarkers to evaluate human exposure to organophosphate pesticides. The objective was to evaluate potential artifacts in urinary DAPs analysis during sample preparation and method calibration. Diluted urine pools were commonly used to prepare calibration standards to minimize the effects due to the complexity of urine matrix. Matrix effects on measurements of DAPs were evaluated by spiking known amount of standards into distilled water, synthetic urine and diluted urine pool. Different matrices resulted in similar concentrations detected for all target compounds, except dimethylphosphate (DMP) with the deviation of measurement as large as eight times the spiked amount. In this study, we also found that urinary particles, which usually appeared after thawing frozen human urine samples, could affect the measurements of DAPs, especially DMP and diethylthiophosphate (DETP). Results of DAPs measurements in three types of sample matrices, i.e. urine without particles, urine with particles and particles only were compared. DETP could be subject to large error during this preparation step. The use of deuterated and ¹³C₁₂-labeled DAPs as internal standards is also evaluated. Overall, these issues can cause misidentification and inaccuracies, which may significantly affect the data quality.     

混凝-超滤短流程工艺处理北方水库原水

采用混凝-超滤膜短流程工艺对大伙房水库原水进行处理,考察其除污染性能和膜污染情况,并对该短流程工艺参数进行优化。结果表明,当利用超滤膜直接过滤原水时,膜污染较重,并且对污染物质的去除率较低;而采用混凝．超滤短流程工艺时,膜污染得到一定程度上的缓解;当絮凝剂投加量为7mg／L、膜清洗周期为30min时,对浊度、CODMn和UV254的去除率分别为95．61％、40．42％和37．12％,出水水质能够满足生活饮用水卫生标准。     

污泥微膨胀状态下短程硝化的实现

为了实现"低氧丝状菌活性污泥微膨胀"和短程硝化的结合,本试验采用SBR反应器,研究了在微膨胀状态下,短程硝化的启动方法和短程硝化启动过程中污泥沉降性的维持策略.分析了水质、pH、DO和温度等环境因素以及混合液流态、曝气方法和进水方式等运行条件对污泥沉降性的影响.结果表明,在pH处于7.2~8.0,温度处于20~25℃时,通过维持低溶解氧和准确控制曝气时间可以逐步在污泥微膨胀状态下实现短程硝化.系统运行160个周期后,亚硝酸盐积累率可从28%逐步上升到80%.通过改变进水体积交换率和辅助调节曝气量的方法可以有效维持活性污泥的沉降性.在污泥微膨胀状态下,VER在0.25~0.33适时调节,可控制污泥容积指数在150 mL/g附近小幅波动.在好氧阶段后期,会出现溶解态总氮浓度的小幅上升.     

4种短链全氟化合物替代物在城市污水处理厂的污染特征研究

全氟辛烷羧酸(perfluorooctanoic acid,PFOA)和全氟辛烷磺酸(perfluorooctyl sulfonate,PFOS)等长链全氟化合物(perfluorinated compounds,PFCs)具有持久性、生物累积性和毒性,近年来发现一些短链PFCs具有相对较短的半衰期,可以成为PFOA和PFOS的替代品,这些物质包括C4和C6结构的PFCs,如全氟丁烷羧酸(perfluorobutanoic acid,PFBA)、全氟己烷羧酸(perfluorohexanoic acid,PFHx A)、全氟丁烷磺酸(perfluorobutyl sulfonate,PFBS)和全氟己烷磺酸(perfluorohexyl sulfonate,PFHx S)。为解析我国城市污水厂短链PFCs污染水平和地域分布特征,本研究调查了我国不同地区17座城市污水处理厂的进水、二沉出水和污泥中4种短链PFCs的分布和浓度水平。结果表明4种短链PFCs、PFOA和PFOS在17座污水厂进水中检出率均为100%(6种目标物单体浓度范围:0.19~274.72 ng·L-1);污泥中PFOS和PFOA检出率为100%(PFOS:2.08~72.31 ng·g-1,PFOA:1.03~24.81 ng·g-1),PFBA、PFHx A检出率为100%(0.60~3.33 ng·g-1),PFBS和PFHx S的检出率分别为42.11%和63.16%。在污水厂进水中,将PFOA和PFOS与其同类的短链PFCs浓度进行比较,发现短链PFCs分别相对于PFOA和PFOS的比例最高可达93.47%和94.57%。4种短链PFCs、PFOA和PFOS的地域分布差异明显,总浓度呈现出华东、华南地区高于西北、东北、华北地区的趋势,其中华东地区调查的污水处理厂浓度最高。污水厂4种短链替代物主要通过污水排放,不同污水厂的日排放总量(污泥和出水)为0.25~273.07 g·d-1,万吨水排放量范围为0.04~1.37 g。研究将为我国全氟化合物替代物污染和控制提供数据基础和科学依据。     

超高效液相色谱-质谱法直接进样测定水中草甘膦和丁基黄原酸

通过优化色谱条件、稀释样品、加入氨水等措施,建立了超高效液相色谱-质谱法直接进样分析地表水及自来水中草甘膦和丁基黄原酸的方法。草甘膦和丁基黄原酸在各自线性范围内线性关系良好,相关系数(R2) 0. 999。方法检出限分别为5. 20(前处理中对样品进行了20倍稀释)和0. 08μg/L,远低于国家标准限值要求。草甘膦和丁基黄原酸的加标回收率分别为73. 8%～92. 3%和85. 0%～113. 0%,样品间的标准偏差均10%,准确度和精密度均满足质控要求。该方法简化了样品前处理过程,成功降低了基质效应对草甘膦和丁基黄原酸测定的干扰。     

典型锥形结构两点响应控制试验研究

目的 研究小长径比结构进行两点振动响应控制时的可行性,提升地面振动模拟真实性.方法 针对一长径比约3:1的短圆锥结构,首先以圆锥表面气动载荷为振动输入载荷,通过数值仿真获得结构在自由状态下内部两点的加速度功率谱密度曲线,再采用激励杆和激励板的形式进行两点激励加载,控制要求的两点加速度响应.将真实响应的控制结果 与常用梯...     

超高效液相色谱-三重四极杆质谱法同时分析沉积物中6种溴代阻燃剂

利用超高效液相色谱-三重四极杆质谱建立了沉积物中6种溴代阻燃剂的分析方法,同时进行了采样分析。以正己烷-二氯甲烷(体积比1∶9)为萃取剂,在100℃下用加速溶剂萃取仪提取沉积物样品,循环3次。萃取液浓缩至2.0 m L,转移至净化柱,用150 m L正己烷-二氯甲烷(体积比1∶2)淋洗。将淋洗液浓缩至近干,加入内标物,定容至1 m L后,用液相色谱-三重四极杆准确定量。方法干重检出限为0.01～0.1 ng/g;替代标回收率为75.6%～98.9%,相对标准偏差为12.0%～13.0%;目标物回收率为70.5%～99.2%,相对标准偏差为2.1%～17.0%。研究区域水体沉积物中的三(2,3-二溴丙基)异氰脲酸酯浓度为未检出～0.14 ng/g,(2,4,6-三溴苯氧基)-1,3,5-三嗪浓度为未检出～0.14 ng/g,十溴二苯醚浓度为0.81～4.36 ng/g,六溴苯浓度为未检出～0.08 ng/g,表明沉积物中新型溴代阻燃剂浓度处于较低水平。     

Characteristics and removal mechanism of the precursors of N-chloro-2,2-dichloroacetamide in a drinking water treatment process at Taihu Lake

• N-Cl-DCAM, an emerging N-DBP in drinking water was investigated. • A new BAC has a better removal efficiency for N-Cl-DCAM precursors than an old BAC. • N-Cl-DCAM precursors are more of low molecular weight and non-polar. • Adsorption of GAC plays a major role in removal of N-Cl-DCAM precursors by an O₃-BAC. N-chloro-2,2-dichloroacetamide (N-Cl-DCAM) is an emerging nitrogenous disinfection by-product (N-DBP) which can occur in drinking water. In this study, an analytical method based on liquid chromatography with tandem mass spectrometry (LC-MS/MS) was developed to validate the concentration of N-Cl-DCAM, which was found to be 1.5 mg/L in the effluent of a waterworks receiving raw water from Taihu Lake, China. The changes of N-Cl-DCAM formation potential (N-Cl-DCAMFP) in the drinking water treatment process and the removal efficiency of its precursors in each unit were evaluated. Non-polar organics accounted for the majority of N-Cl-DCAM precursors, accounting for 70% of the N-Cl-DCAM FP. The effect of conventional water treatment processes on the removal of N-Cl-DCAM precursors was found to be unsatisfactory due to their poor performance in the removal of low molecular weight (MW) or non-polar organics. In the ozonation integrated with biological activated carbon (O₃-BAC) process, the ozonation had little influence on the decrease of N-Cl-DCAM FP. The removal efficiency of precursors by a new BAC filter, in which the granular activated carbon (GAC) had only been used for four months was higher than that achieved by an old BAC filter in which the GAC had been used for two years. The different removal efficiencies of precursors were mainly due to the different adsorption capacities of GAC for individual precursors. Low MW or non-polar organics were predominantly removed by GAC, rather than biodegradation by microorganisms attached to GAC particles.     

Excretion stereoselectivity of triticonazole in rat urine and faeces

Abstract

The purpose of this study was to study the excretion stereoselectivity of triticonazole enantiomers in rat urine and faeces. Six male Sprague-Dawley (SD) rats were administrated 50?mg/kg rac-triticonazole. Rats urine and faeces were separately and quantitatively collected at the following intervals: 0–3, 3–6, 6–9, 9–12, 12–24, 24–36 and 36–48?h. The faeces samples were homogenized in an aqueous solution containing 0.2% DMSO at the ratio of 1?g: 40?mL. An aliquot of 100?μL rats urine or faeces homogenate was spiked and mixed with 6.0?μL of 1.00?μg/mL flusilazole as an internal standard. The triticonazole enantiomers in urine and faeces were determined by using an HPLC/MS–MS after samples preparation. The excreted amounts of enantiomers in the urine showed a significant difference (P?<?0.05) except for 3–6?h. The cumulative excretion rate (Xu_0→24) in urine was 26.43?±?0.08% and 37.58?±?0.11% for R-(?)- and S-(+)-triticonazole, respectively, indicating high enantioselectivity (P?<?0.001). The cumulative excretion rate (Xu_0→72) in faeces was 6.93?±?0.03% and 6.77?±?0.03% for R-(?)- and S-(+)-triticonazole, respectively, without a difference. The results showed that the total cumulative percentage of triticonazole enantiomers accounted for in urine and faeces was 64.00?±?0.13% and 13.70?±?0.32%, the urinary excretion of R-(?)- and S-(+)-triticonazole were significantly different and S-(+)-triticonazole was preferentially excreted. However, the faecal excretion of the enantiomers showed no difference.