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1.
建立了一种泥沙水样中分离微塑料纤维和去除泥沙的方法。选取聚酰胺6(Polyamide 6,PA)、丙烯腈-丁二烯-苯乙烯共聚物(Acrylonitrile butadiene styrene copolymers,ABS)、聚丙烯(Polypropylene,PP)颗粒,制备长度(1±0. 25) mm,宽度(200±30)μm的微塑料纤维;分别混合不同质量(0,0. 01,0. 05,0. 25,1. 25,6. 25 g)经30%过氧化氢消解和饱和氯化钠(1. 2 g/m L)、碘化钠溶液(1. 8 g/m L)浮选后的自然泥沙;以探究在不同泥沙质量下,静置阶段投加氯化钠颗粒对玻璃漏斗中微塑料纤维分离效率以及泥沙去除率的影响,并与不投加氯化钠和容量瓶浮选法作比较。结果表明,在静置阶段添加氯化钠颗粒效果较优,对3种微塑料纤维的平均分离效率和泥沙的平均去除率分别为87. 78%和98. 33%。实验结论可为微塑料分离提取方法的优化提供参考。  相似文献   

2.
王斌 《中国环境监测》2016,32(5):116-119
免疫磁性微球(SMPPA)应用于水样中吲哚美辛的分离富集,并应用高效液相色谱法对吲哚美辛进行测定。在优化的淋洗和洗脱条件下,70%甲醇和10%甲醇分别作为洗脱液和淋洗液,其回收率能达到90%。选择了湖水、河水、自来水、污水厂进口水以及医院排水为真实样品进行测定,其中湖水、河水、自来水3种真实水样中未能检测出吲哚美辛,污水厂进口水以及医院排水中吲哚美辛的含量分别为0.762、35.4 ng/m L。对这5种水进行加标回收吲哚美辛,加标回收率为92.7%~113%,RSD为1.09%~7.73%。该方法具有简便、快速、特异性等特点,能有效地分离富集水样中的目标物,对其他目标物具有广泛的实际应用价值。  相似文献   

3.
建立了固相微萃取(SPME)与气相色谱-三重四极杆质谱法(GC-MS/MS)联用直接测定水体中16种多环芳烃的快速分析方法。通过实验,对固相微萃取纤维涂层的选择、萃取时间、萃取温度等萃取条件以及碰撞电压等参数进行了优化。实验结果表明,采用涂层厚度为100μm的聚二甲基硅氧烷(PDMS)萃取头,以350转/分钟(r/min)40℃下搅拌萃取40min,在GC进样口经280℃热解析6min后,以气相色谱-三重四极杆质谱的多反应监测(MRM)模式检测。在0.2~4.0μg/L的线性范围内,该方法对水中16种PAHs所得的回归方程均具有较好的线性关系,相关系数r值为0.9953~0.9995,检出限为0.001~0.02μg/L。16种PAHs的0.4μg/L加标水样的回收率平均值范围在71%~115%之间,6次平行测定的RSD范围在3.3%~15.6%之间。  相似文献   

4.
于2019年10月,对江苏省(连云港、盐城和南通3市)近岸海域6个站位进行了1个航次的表层海水微塑料采样,监测分析了微塑料的粒径、丰度和组分分布情况。结果表明,江苏省近岸海域表层海水中微塑料污染广泛存在,监测站位检出率100%。微塑料粒径分布为0.02~4.80 mm,微米级微塑料占比最高(总体粒径占比83.4%),6个站位中15,24,36和37站位毫米级微塑料占比较高,呈现距离海岸越近毫米级微塑料占比越高的趋势。微塑料的丰度为0.06~1.18个/m3,平均丰度为0.33个/m3,站位丰度排序为:36站位<26站位<37站位<24站位<15站位<59站位,其中站位最大丰度为站位最小的19.6倍。6个站位中,59站位的微塑料组分最多。所有微塑料组分中,乙烯醋酸乙烯酯共聚物(EVA)占比最高。微米级微塑料共有16种塑料组分,其中EVA占49.0%,聚氨基甲酸乙酯(PU)占24.3%;毫米级微塑料共有5种塑料组分,其中聚苯乙烯(PS)占比最高(43.3%)。  相似文献   

5.
固相微萃取-气相色谱法测定水中酞酸酯类化合物   总被引:1,自引:1,他引:0  
建立了固相微萃取(SPME)-气相色谱(GC)法分析环境水样中痕量酞酸酯类化合物(PAEs)的方法。选用65 μm PDMS/CVB萃取纤维,在磁力搅拌转速为700 r/min、萃取温度为60℃条件下,对水样中的PAEs萃取富集50 min,然后直接注入GC进样口,在 250℃ 温度下解吸1.5 min后进行分析测定,6种PAEs能得到充分提取和分离。方法的检出限为0.010 8~0.029 3 μg/L。对水样进行3个质量浓度水平(0.025、0.125、0.25 μg/L)的加标实验,加标回收率为41.79%~132.80%,RSD为6.53%~18.74%(n=7),用该法测定了某制药厂的实际水样,测得DBP含量为0.018 6 μg/L,DEHP、 DMP、DEP、DOP、BBP均未检测到。  相似文献   

6.
高效液相色谱法检测水中微囊藻毒素的实验条件优化   总被引:1,自引:0,他引:1  
通过实验优化高效液相色谱检测水中微囊藻毒素的方法,对水样前处理过程中使用的固相萃取柱、淋洗剂、洗脱剂及浓缩定容方式等进行了选择.用流动相为V(1.25%TFA水溶液)∶V(甲醇)=40∶60的溶液洗脱,MC-RR和MC-LR在15 min内有较好的分离,工作曲线的范围为0.1 mg/L~10 mg/L,方法检测限为0.1 μg/L,两者的回收率分别为98.1%和101%.测定方法简易、可靠和实用.  相似文献   

7.
对石墨炉原子吸收法测定水中铊的分析条件进行优化,并比较不同前处理方法对测定结果的影响。结果表明仪器的最佳分析条件为:灰化温度和原子化温度分别为700和1 600℃,进样量为40μL,基体改进剂为0.5%的钯与硝酸镁。直接进样、MIBK萃取法和铁沉淀富集3种前处理方法对应的检出限分别为0.76,0.07和0.02μg/L;分别测定5,0.5和0.1μg/L含铊水样,其相对标准偏差分别为4.2%,6.1%和8.4%,加标回收率分别为92%,91%和88%,即3种样品前处理方式下,石墨炉原子吸收法对环境水样中铊均具有较好的测定效果。直接进样法适用于铊浓度较高的水样,MIBK萃取法和铁沉淀法则适用于较清洁水样。  相似文献   

8.
高效液相色谱-柱前衍生法测定水中有机磷除草剂   总被引:3,自引:0,他引:3  
建立了水样中痕量草甘膦、草铵膦和氨甲基磷酸的FMOC柱前衍生-高效液相色谱-荧光检测分析方法。草甘膦,草铵膦和氨甲基磷酸的平均加标回收率分别为94.2%、90.8%、98.6%;相对标准偏差分别为4.8%、0.68%、2.8%;方法的定性下限和定量下限分别为0.05、0.04、0.009μg/L和0.16、0.12、0.03μg/L。水样放置两天后,水样中的草甘膦、草铵膦分别降解了17.8%和19.5%,而水样经过衍生后在5天内是稳定的。  相似文献   

9.
采用固相萃取-高效液相色谱-串联质谱法(SPE-UPLC-MS-MS)测定自然水体中的10种典型药物污染。比较了2种萃取柱HLB和C18的富集效果,并对水样pH、萃取柱的淋洗溶剂及水样体积进行了优化。结果表明,采用HLB小柱进行富集净化,水样体积为500 mL,调节pH=3.0,95%甲醇洗脱,在0~200μg/L范围内10种药物的标准曲线线性关系良好(r≥0.999),方法检出限0.5~2.0 ng/L,精密度高(RSD10%),加标回收率为64.3%~100.7%。经过对太湖和某污水厂排水口水样的测试,表明该方法适用于自然水体药物的快速检测,同时大部分药物被检出,说明选择的10种目标药物及建立的检测方法对研究中国水体药物污染具有一定的参考价值。  相似文献   

10.
系统研究了地表水中四乙基铅的吹扫捕集-气相色谱/质谱分析方法,水样的加标回收率为82%~105%,最低检测限(3σ)及最低定量限(10σ)分别为0.015μg/L和0.05μg/L,0.1μg/L的水样重复进样(n=7)的相对标准偏差为5.4%。利用该方法对浙江省主要城市饮用水源地地表水中四乙基铅进行分析,检测结果均低于检出限。  相似文献   

11.
Occurrence, variation and behaviour of nonylphenol (NP) and octylphenol (OP) were studied in surface water and groundwater in Guiyang, Guizhou Province, southwestern China. Discharge of wastewater from Guiyang City was the main source of alkylphenols (APs) entering the aquatic environment. The concentrations of NP and OP in river water ranged from 40 to 1582 ng L(-1) and from below the lowest limit of detection (LOD) to 67 ng L(-1), respectively. NP and OP were also detected in groundwater. Both NP and OP exhibited spatial and temporal variations in river water and groundwater. It was found that concentrations of NP and OP in river water was low upstream and dramatically increased downstream, and higher concentration of NP was found in winter compared to that in summer. Proportions of NP and OP were trapped by suspended particulate matter (SPM), which accounted for 7.6-50.0% and 3.4-25.6% of their total concentration in the river water system, respectively. Seasonal changes in water flow were responsible for the temporal variations of APs. To determine the behaviour of APs along the river, a mass balance equation based on chloride was used. The results showed that a mixing process was the predominant factor to determine upstream APs concentrations; while the discharge of wastewater controlled the concentrations of APs downstream. Considering the adverse effect of APs on organisms, combined effect modeling was used to assess the toxicity to fish. It was found that the predicted mixture effect for APs in river water on fish vitellogenin induction was low upstream and medium downstream, respectively.  相似文献   

12.
This study quantifies the regional distribution of the micropollutant benzothiazole (BT) in river water by sampling 15 river sites in the Schwarzbach watershed (about 400 km(2)) from November 2008 to February 2010. Additionally, wastewater samples from three municipal wastewater treatment plants (WWTPs) in Germany were analyzed. BT was detected in all wastewater influent and effluent samples as well as in all river water samples collected downstream of wastewater discharge. This corroborates the ubiquitous occurrence of BT in the aqueous environment. Concentrations were between 58 and 856 ng L(-1) in the river water. The observed mean concentration at the outlet of the investigated catchment was 109 ng L(-1). With only a few exceptions, temporal and spatial variations of BT concentrations in river water were low. Rather similar BT concentrations over a wide range of river discharge indicate that dilution along the mainstream is negligible and, thus, supports the hypothesis that paved surface runoff during rain events is an important BT source not only for wastewater influent but also for river water. This was supported by detecting the highest BT concentrations at sampling locations close to the dense highway network around the city of Frankfurt. Since BT was also detected in river water collected from locations that were clearly unaffected by wastewater effluent discharge, surface runoff must be considered as a diffuse source of BT in river water.  相似文献   

13.
对80个不同水体样品进行了环境雌激素检测,共有42个样品为阳性(阳性率52.5%),阳性样品主要来自于医疗废水、市政排污口、污水处理厂及与工业污染源废水,水源水中未检出。42个阳性样品检测值均超过EPA标准规定的壬基酚4 d平均浓度限值(6.6μg/L),其中12个样品检测值超过了该标准中规定的壬基酚小时平均浓度限值(28μg/L)。  相似文献   

14.
The presence of the anesthetic lidocaine (LDC), the analgesic tramadol (TRA), the antidepressant venlafaxine (VEN) and the metabolites O-desmethyltramadol (ODT) and O-desmethylvenlafaxine (ODV) was investigated in wastewater treatment plant (WWTP) effluents, in surface waters and in groundwater. The analytes were detected in all effluent samples and in only 64% of the surface water samples. The mean concentrations of the analytes in effluent samples from WWTPs with wastewater from only households and hospitals were 107 (LDC), 757 (TRA), 122 (ODT), 160 (VEN) and 637 ng L(-1) (ODV), while the mean concentrations in effluents from WWTPs treating additionally wastewater from pharmaceutical industries as indirect dischargers were for some pharmaceuticals clearly higher. WWTP effluents were identified as important sources of the analyzed pharmaceuticals and their metabolites in surface waters. The concentrations of the compounds found in surface waters ranged from 相似文献   

15.
The present paper reports a detailed study that is based on the monitoring of naproxen, ibuprofen, and diclofenac in Mbokodweni River and wastewater treatment plants (WWTPs) located around the city of Durban in KwaZulu-Natal Province of South Africa. Target compounds were extracted from water samples using a multi-template molecularly imprinted solid-phase extraction prior to separation and quantification on a high-performance liquid chromatography equipped with photo diode array detector. The analytical method yielded the detection limits of 0.15, 1.00, and 0.63 μg/L for naproxen, ibuprofen, and diclofenac, respectively. Solid-phase extraction method was evaluated for its performance using deionized water samples that were spiked with 5 and 50 μg/L of target compounds. Recoveries were greater than 80% for all target compounds with RSD values in the range of 4.1 to 10%. Target compounds were detected in most wastewater and river water samples with ibuprofen being the most frequently detected pharmaceutical. Maximum concentrations detected in river water for naproxen, ibuprofen, and diclofenac were 6.84, 19.2, and 9.69 μg/L, respectively. The concentrations of target compounds found in effluent and river water samples compared well with some studies. The analytical method employed in this work is fast, selective, sensitive, and affordable; therefore, it can be used routinely to evaluate the occurrence of acidic pharmaceuticals in South African water resources.  相似文献   

16.
A solid phase extraction (SPE) method has been developed and applied in conjunction with a previously reported liquid chromatography tandem mass spectrometry (LC-MS-MS) procedure for the determination of illicit drugs and abused pharmaceuticals in treated wastewater and surface water samples at the ng L(-1) level. A full method validation was also performed and determined levels of analytical sensitivity were found to lie in the 1-10 ng L(-1) range using river water as a test sample matrix and a sample size of 500 mL. The developed procedure was successfully applied for the determination of the chosen analytes in wastewater treatment plants in Dublin, Ireland and rapidly expanding commuter towns in the surrounding counties. Cocaine was detected in 70% of the collected samples in the range of 25-489 ng L(-1), its primary metabolite, benzoylecognine (BZE) was also detected in the range of 22-290 ng L(-1). Other substances detected included morphine, Tempazepam and the primary metabolite of methadone.  相似文献   

17.
A simple on-line method was developed for the analysis of pharmaceuticals, pesticides and some metabolites in drinking, surface and wastewater samples. The technique is based on the use of on-line solid-phase extraction combined with liquid chromatography electrospray tandem mass spectrometry with positive electrospray ionization (LC-ESI(PI)-MS/MS). The injection of only 1 mL of filtered water sample is used with a total analysis time of 20 min, including the period required to flush the SPE cartridge with organic solvent and reconditioning the LC column. Method detection limits were in the range of 2 to 24 ng L(-1) for the compounds of interest, with recoveries from 87 to 110% in surface as well as wastewater samples. Matrix effects were observed for some compounds without exceeding more than 25%. All results displayed a good degree of reproducibility, with relative standard deviations (RSD) of less than 12% for all compounds. Moreover, at least 200 samples were analyzed without altering the performance of the pre-concentration column. This method was preferred over traditional off-line procedures because it minimizes tedious sample preparation, increases productivity and sample throughput. The analysis of various water and wastewater samples showed that caffeine, carbamazepine and atrazine could be detected in all the samples analysed and the selected compounds are always present in at least one of the sample types.  相似文献   

18.
Environmental occurrence of CECs poses a great threat to both aquatic life and human health. The aim of this study was to optimize and validate SPE/LC-(ESI)MS-MS method for simultaneous quantitative monitoring of two sub-classes of CECs (pharmaceuticals and hormones) and to estimate the concentrations of select CECs in environmental water samples. For all the tested analytes, recoveries in laboratory reagent water were greater than 81%. Average percent (relative standard deviation) RSD of the analytes in recovery, repeatability, and reproducibility experiments were ≤?10%. Determination coefficients (r2) of primidone, diclofenac, testosterone, and progesterone were estimated to be 0.9979, 0.9972, 0.9968, and 0.9962, respectively. Limits of detection (LOD) for primidone, diclofenac, testosterone, and progesterone were 4.63 ng/L, 5.36 ng/L, 0.55 ng/L, and 0.88 ng/L, respectively. Limits of quantification (LOQ) for primidone, diclofenac, testosterone, and progesterone were 14.72 ng/L, 17.06 ng/L, 1.766 ng/L, and 2.813 ng/L, respectively. Average recoveries in environmental water and wastewater samples were greater than 74% and RSD were ≤?7%. Trace levels (68.33–125.70 ng/L) of primidone were detected in four environmental water samples, whereas diclofenac was not detected in any of the tested sample. Trace levels of progesterone were observed in two environmental samples (16.64 –203.73 ng/L), whereas testosterone was detected in STP inlet sample (178.16 ng/L).  相似文献   

19.
近年来,由个人护理品及废旧塑料直接或间接产生的微塑料不断地在各种环境介质中被检出,且微塑料会对生态系统产生各种危害,因此对微塑料的研究受到越来越广泛的关注。阐述了微塑料在水体、沉积物、沙滩和生物体中的赋存情况,介绍了微塑料的采集与分离方法,以及定性与定量分析方法。指出微塑料对环境及生物体产生的危害,提出现阶段研究存在的主要问题,并对今后的研究方向进行了展望。  相似文献   

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