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溴代阻燃剂的分析方法及其在黄河三角洲土壤中的污染特征
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摘要
本论文在全面综述环境中溴代阻燃剂(BFRs)的富集、净化与分析方法、来源及源解析技术、吸附/解吸机理、土壤特性参数影响污染物分布的基础上,针对国内外目前尚无通用分析方法的现状,经过系统研究样品前处理技术并全面优化影响回收率与灵敏度的因素后,建立了环境水样中四溴双酚A (TBBPA)、六溴环十二烷(HBCDs)液相分散微萃取联合液相色谱串联质谱联用技术的分析方法;建立了环境土壤中多溴联苯醚(PBDEs)、TBBPA与HBCDs的基于基质固相分散联合色谱质谱联用技术的分析方法;制订了区域土壤采样方案,研究得到了黄河三角洲地区土壤中PBDEs. TBBPA与HBCDs的组成特征、分布特征、污染现状及其三维空间分布规律;利用相关性分析、聚类分析及主成分分析对黄河三角洲土壤中BFRs的来源与分布影响因素等进行了简要分析,从而建立了土壤环境中BFRs污染源的识别和解析方法;找到了影响BFRs分布的主要土壤坏境特性因素。本研究为进一步揭示土壤环境中BFRs的来源、迁移转化机理和归趋研究奠定了理论基础,同时可为我国新型溴代阻燃剂污染控制和增强环境履约能力提供技术与科技支撑。论文研究内容及结论如下:
     (1)利用室温离子液体(RTIL)液相分散微萃取技术与液相色谱串联质谱联用技术(TCILDLME-LC-MS-MS),建立了水样中TBBPA与HBCDs简便、环境友好、灵敏的分析方法。实验中用几十微升的室温离子液体为萃取剂,代替了传统方法使用的数百毫升有毒有机试剂,避免了环境污染,节省了费用,减小了样品用量,缩短了样品前处理的时间,同时大大减少了劳动强度。对实际环境水样的分析的结果表明该方法精密度高、准确性好、检测限低,在环境监测和研究领域具有广阔的应用前景。
     研究结果为:①TBBPA的最优条件:70μL[C6mim][PF6]、萃取温度60℃、萃取时间15min、水样溶液pH4、0%盐浓度。在上述条件下,空白样品基质加标回收率为72.4-103.9%,相对标准偏差为3.31-8.68%,方法检测限为50ng/L,并对三个实际水样进行了测定。②HBCDs的最优条件:70μL[C6mim][PF6]、萃取温度75℃、萃取时间30min、水样溶液pH6、0%盐浓度。在上述条件下,空白样品基质加标回收率在77.2-99.3%之间,精密度2.2-8.43%,方法检测限为10ng/L,并成功应用于实际水样的分析。
     (2)建立了基于竹炭为分散吸附剂的基质固相分散联合气相色谱负化学源质谱联用技术(MSPD-GC-NCI-MS)的快速分析土壤中8种PBDEs的方法。最优条件为:1.0g土壤与0.5g竹炭混合,用10mL二氯甲烷洗脱。在此条件下,空白加标回收率为71.7-105.9%,相对标准偏差(RSD)为3.57-9.88%,方法检测限分别为10-80ng/kg,满足美国1614方法草案的要求。
     (3)建立了基于竹炭为分散吸附剂的基质固相分散同位素稀释联合液相色谱串联质谱联用(MSPD-ISD-LC-MS-MS)技术快速分析土壤中TBBPA与HBCD三种异构体的方法。最优条件为:质谱干燥气温度280℃,柱温50℃,0.5g土壤与0.5g竹炭混合,使用8mL二氯甲烷与乙腈的混合液洗脱(体积比9:1)。在上述条件下,空白加标回收率为72.8-102.2%,相对标准偏差(RSD)为3.4-9.8%,TBBPA、α-、β-、γ-HBCD方法检测限分别为11、75、10与4ng/kg。以上数据说明,该方法可满足检测土壤中低浓度的TBBPA与HBCDs的要求。
     基质固相分散技术极大的缩短了样品前处理时间,将传统实验20多小时的样品前处理缩短为20分钟;LC-MS-MS分析技术中应用同位素稀释法消除了基质效应的影响,实验结果说明所建立的方法简单、快速、检测限低,适合于实际批量样品的常规分析,具有十分重要的实际应用价值。
     (4)经过对黄河三角洲地理概况、自然环境及社会经济发展的简要分析,制订了区域土壤采集方案。利用所建立的分析方法,对所采集的土壤样品分析后,得到黄河三角洲表层土壤中BFRs的浓度及组成特征:
     ①土壤中8种PBDEs同系物均有检出,PBDEs总浓度为0.944μg/kg, BDE209浓度为0.775μg/kg,占总量的72.5%,是PBDEs支配地位的同系物,说明PBDEs污染主要来自于Deca-BDE; BDE28、47、99、153及BDE183等低溴代联苯醚,代表了penta-BDE与octa-BDE对研究区PBDEs的贡献。土壤中的penta-BDE的组成模式与其他研究大体相似,但又有所区别。本研究BDE47与BDE99的比值与商品Great lakeDE-71中比值较为接近,说明Great lake DE-71工业品的使用或相似产品的生产可能是黄河三角洲土壤penta-BDE的重要来源。
     ②HBCDs的浓度及组成特征:HBCDs,总浓度为3.734μg/kg。α-与γ-HBCD同时检出,二者浓度与检出频次相关性,γ-HBCD为主要异构体,丰度为58.21%。HBCDs异构体的组成特征,说明研究区存在HBCDs工业品的近距离排放来源,但特定采样点也存在着其他输入途径或发生了降解、转化等环境行为变化;TBBPA的浓度为0.601μg/kg。
     (5)黄河三角洲土壤中BFRs的空间分布特征:
     ①纵向上PBDEs与HBCDs的含量随纬度的下降而逐渐增大,但TBBPA的上升趋势不明显,说明黄河三角洲土壤中PBDEs与HBCDs可能主要来源于南部莱州湾BFRs生产过程中污染源的LART, TBBPA则可能来自采样点当地直接释放;
     ②横向上黄河三角洲土壤中BFRs的浓度随黄河流向而逐渐减小,但三种BFRs的具体变化不完全一致,说明各类BFRs的源-大气-土壤的转化效率或输入途径存在区别;
     ③垂向剖面土壤越深,BFRs含量越低;随剖面深度增大,低溴代BDEs同系物丰度升高,HBCDs异构体组成变化没有明显特征。
     (6)污染水平比较:黄河三角洲土壤中PBDEs的浓度与其他中国报道的非点源来源地区土壤中的浓度接近,处于世界土壤PBDEs污染的较低水平;TBBPA的污染水平低于荷兰等国外河流沉积物及武汉市垃圾填埋场土壤中浓度,与美国、挪威湖泊沉积物中的含量相当;HBCDs的污染水平与我国哈尔滨市、广州市城市与农田土壤含量接近。总体结论为黄河三角洲土壤中BFRs含量较低,与我国城区及国外背景点污染水平接近,PBDEs污染低于USEPA建议的标准限值;
     (7)黄河三角洲土壤PBDEs、BDE209、TBBPA及HBCDs的蓄积量分别为:15.29t、12.55t、9.73t与60.49t。说明BFRs蓄积量已达到一定水平,建议必须尽早建立起相应的控制、预警和消减技术,将BFRs可能造成的环境危害降至最低。
     (8)通过相关性分析、聚类分析与主成分分析,得到以下结论:①deca-BDE与HBCDs对黄河三角洲土壤中BFRs有较大的贡献,但同时deca-BDE在环境中经自然光照或生物降解来源也不能忽视;②deca-BDE对PBDEs污染贡献最大,penta-BDE对∑low(BDEs)贡献率较大,octa-BDE对∑low(BDEs)贡献较小;③LRAT对土壤中TBBPA贡献较小,TBBPA主要来源于当地生活与生产活动向周围环境的直接释放;④HBCDs与deca-BDE均通过大气近距离输送而沉降于表层土壤,可能来源于莱州湾BFRs生产区,∑low(BDEs)可能为黄河三角洲外大气长远距离的输入。
     (9)通过对黄河三角洲地区土壤性质与BFRs污染分布的相关性分析,可以看出,土壤TOC与BDE28、BDE47、BDE153及∑low(BDEs)呈显著正相关,与∑PBDEs、TBBPA及HBCDs呈弱正相关关系。土壤中水溶性盐含量与BFRs很弱的负相关,pH值及硫含量与BFRs没有明显的相关性。因此,土壤中TOC含量是影响BFRs分布的主要因素。
In this study, the former researches about the analytical methods, advanced progress of BFRs in environmental and organism matrix, source apportionment approaches and distribution trends in soils were reviewed comprehensively. The factors influencing recovery were investigated and optimized systematically, an rapid and accurate analytical method for determination of TBBPA and HBCDs in environmental water samples by liquid dispersive microextraction prior to with liquid chromatography coupled with tandem quadrupole mass spectrometry was developed; Another rousted analytical approach for determination of PBDEs, TBBPA and HBCDs in environmental soil was proposed based on the matrix solid phase dispersive technique; The sampling scheme was instituted, and the compositions, distribution trends, pollution levels and spatial distribution of PBDEs, HBCDs and TBBPA in soil from Yellow River Delta were investigated in detail and obtained; The source apportionment of BFRs in soil was carried out by correlation analyses, hierarchical cluster analysis and principal component analysis; The influences of the soil characteristics parameters to distribution of BFRs in soil was studied and the controlling factor was founded out by correction analysis. The study provided a method and theory basis for the research on the mechanism of transportation, transformation and fating of BFRs in soil. This dissertation included the following contents and conclusions:
     (1).Based on temperature controlled ionic liquid dispersive liquid phase microextraction coupled with liquid chromatography tandem quadrupole mass spectrometry (TCILDLME-LC-MS-MS), two rapid, simple, environmental, sensitive analytical methods for determination of TBBPA and HBCDs were established.
     ①The final optimum conditions for determination of TBBPA are70μL[C6mim][PF6], extraction temperature60℃, extraction time15min, solution pH4and0%salt content. Under above condtions, excellent linearity of TBBPA was obtained in the range of0.5-50μg/L with correlative coefficient (R)0.9987. The limit of detection of TBBPA was0.05μg/L and the relative standard deviation (RSD) was7.70%(n=6). The satisfactory of TBBPA spiked recoveries were in the range of92.4-103.9%and RSDs were in the range of3.31-8.68%.②The final optimum conditions for determination of HBCDs are70μL [C6mim][PF6], extraction temperature75℃, extraction time30min, solution pH6and0%salt content. Under above condtions, good linear relationship, sensitivity and reproducibility of HBCDs were obtained. All the limits of detection for the three diastereomers were10ng/L. The linear range was obtained in the range of1-100μg/L for the total amount of three HBCD diastereomers. It was satisfactory to analyze real environmental water samples with the recoveries ranging from77.2%to99.3%.
     The advantages of TCILDLME-LC-MS-MS are low cost, avoiding environmental pollution, decreasing the amount of sample, saving the pretreatment time of sample and lessening the heavy labour intensity through the hundreds milliliters organic solvent replaced by several microlitres IL. The results from analysis of the real water samples demonstrated that the proposed methods are high precision, good accuracy and lower level of detection, and can be used widely in environmental monitoring and research.
     (2).Based on the matrix solid phase dispersive using bamboo charcoal as dispersive sorbent prior to gas chromatography coupled with negative chemical ionic source mass spectrometry (MSPD-GC-NCI-MS), a rapid and sensitive method for determination of PBDEs in soil was developed, and several factors influencing the recovery were investigated and optimized in detailed. Under the optimum condiciotns, the spiked recovery of the PBDEs was in the range71.7-05.9%, and the limits of detection varied from10to80ng/kg (dry weight). Excellent linearity with correlation coefficients (R2) of0.9992-0.9999was obtained over the concentration range of0.10-500μg/kg, except for BDE209, for which the effective concentration range was1.0-5000μg/kg. The results demonstrated that this method can satisfied the requirements of USPEA method1614.
     (3) An analytical method for determination of TBBPA and HBCD diastereoisomers in soil by MSPD isotopic dilution prior to liquid chromatography coupled with tandem quadrupole mass spectrometry (MSDP-ISD-LC-MS-MS) was proposed. Under the final conditions, the spiked recovery at4,20,80μg/kg level for TBBPA, α-、β-and γ-HBCD were in the range72.8-98.0%,76.8-96.4%,101.9-102.2%and78.1-100%, respectively. The limits of detection were11,75,10,4ng/kg (dry weight) for TBBPA, α-、β-and γ-HBCD, respectively. Excellent linearity with correlation coefficients (R2) of0.996-0.999was obtained over the concentration range of0.80-80μg/kg. The developed method was successfully applied for determination of real soil samples from Laizhou Bay and Yellow River Delta. The results from real samples indicated that the method is sensitive and accurate and suitable for routine analysis.
     MSPD technique has many merits, including the rapidness, simplicity, low cost and easy operation. The pretreatment time decreased from several hours in conventional method to twenty minutes, to save time and diminish the labour intensity. The isotopic dilution technique can avoid the matrix effects satisfactorily. These methods can be used widely in routine environmental monitor and research in the future.
     (4).Through a brief analysis of the geography situation, the natural environment, social and economic development of Yellow River Delta, sampling scheme of regional soil was worked out. After analysis of BFRs in soil samplesusing the proposed analytical method, the composition characteristics of BFRs in the surface soil from Yellow River Delta were obtained and as follows:
     ①PBDEs concentration was0.944μg/kg; the concentration of BDE209was0.775μg/kg, accounting for72.5%of the total PBDEs, and is the dominant congener which indicated that PBDEs pollution mainly comes from Deca-BDE; Low brominated biphenyl ether, including BDE28,47,99,153and BDE183, was on behalf of penta-BDE and octa-BDE contributions to the research area of PBDEs. Patterns of penta-BDE in soil are similar with literatures, but slightly different. In this study, the ratio of BDE47and BDE99and Great lake DE-71commodity ratio is closer, which illustrated that the use of Great Lake DE-71industrial products or similar products may be an important source of soils in the Yellow River Delta.
     ②The concentration of TBBPA in soil in the Yellow River Delta is0.601μg/kg; HBCDs concentration was3.734μg/kg with α-and γ-HBCD simultaneity detection. The concentrations of two diastereoisomers showed the correlation although γ-HBCD as the major isomer with accounting for58.21%of HBCDs. Composition of HBCDs diasteroisomers indicated the emission source of HBCDs industrial products in the study area, however, the degradation, transformation or other environmental change maybe exist in the specific sampling sites.
     (5) Spatial distribution characteristics of BFRs in soils from Yellow River Delta:the concentrations of PBDEs and HBCDs in longitude increased with latitude decreasing gradually, but the increasing trend of TBBPA is not obvious, indicating that PBDEs and HBCDs in the Yellow River Delta mainly sourced from the southern Laizhou Bay BFRs production pollution source by long air routine transfer (LART). TBBPA may come from the sampling point local direct release. The concentrations of BFRs in soil from Yellow River Delta in the horizontal flow with the Yellow River gradually decreased, however, the specific changes of three kinds of BFRs are not completely consistent, which illustrated the transformation efficiency of BFRs source air-soil or input pathways existed differently. Regarding the vertical profile of BFRs, with the increase of soil depth, the concentration of BFRs decreased gradually. Specially, the abundance of low brominated BDE congeners increased, and the composition of HBCD isomers did not significantly change.
     (6).The pollution level was compared with other researches reported. The concentration of BFRs in Yellow River Delta is close to the similar in neighboring region and many non-point source area in China, and much lower than several regions with obviously BFRs pollution in the world. The pollution levels of TBBPA is lower than in the sediment in Netherland and other foreign river, and also lower than in Wuhan City landfill, however, it is comparable with the lake sediments in American and Norway. The pollution level of HBCDs in soil from Yellow River Delta is close to the urban and farmland soil in Harbin and Guangzhou in China. The overall conclusions are that the BFRs burden in soil of Yellow River Delta is low and comparable with other cities in China and foreign background, and less than USEPA recommended limited standards.
     (7).The accumulation and inventory of PBDEs, BDE209, TBBPA and HBCDs in soil from Yellow River delta were15.29t,12.55t,9.73t and60.49t, respectively. The results show that inventory of BFRs has reached a certain level. Therefore, the proposal of the corresponding control must to bring forward as early as possible, and early warning and mitigation techniques should be carried out to reduce the environmental hazards caused by BFRs to a minimum.
     (8).Through the correlation analysis, cluster analysis and principal component analysis, the following conclusions were obtained and as follows:②Deca-BDE and HBCDs have greater contribution to the pollution of BFRs in soil from Yellow River Delta, however, the debrominated transformation of Deca-BDE in the environment with natural light or biodegradable as source cannot be ignored;②Regarding PBDEs source contribution, Deca-BDE has the predomination of PBDEs. Regardingow(BDEs), penta-BDE has domination contribution, otherwise, octa-BDE has second contribution onow (BDEs).③LRAT mode of TBBPA has the smaller contribution, and the main source of TBBPA in research area is the directly releasing from the neighboring production activities.④The migration path of HBCDs and deca-BDE may be the atmospheric near distance transportation to deposit in the surface soil, including the production area of BFRs in Laizhou Bay. However,∑low (BDEs) should be deriving from the long distance input.
     (9).From the correlation analysis between soil properties and BFRs pollution distribution, the results are that TOC has a significant positive correlation with∑low(BDEs), including BDE28, BDE47, BDE153, and a weak positive correlation with PBDEs, TBBPA and HBCDs. Soil dissolved salt is negatively correlated with BFRs, and no obvious correlation on pH value and sulfur content with BFRs. Therefore, TOC content in soil is the main factors influencing the distribution of BFRs.
引文
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