邻苯二甲酸酯在浅层含水层沉积物中的吸附特征研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
环境激素是指环境中存在的一类可以改变人类和动物的内分泌系统,导致生殖、发育和行为异常的化学物质。由于环境激素的内分泌干扰效应及对人类的危害,对环境内分泌干扰物的研究已成为国际研究的新热点。
     邻苯二甲酸酯是环境激素类物质中一类化合物,它主要用作增塑剂。近年来,随着塑料制品的大量生产和使用,邻苯二甲酸酯类物质不断进入环境,已经成为全球最普遍的一大类污染物。其对生物和人类的侵害主要通过呼吸、饮食和皮肤接触进入人体内,对人体健康造成危害。由于PAEs与塑料基质之间没有形成化学键,而是以氢键和范德华力连接,接触到合适的有机溶剂便会溶解出来,对环境、生物和食品造成污染。国内外有很多报道在大气、土壤、饮用水甚至地下水中检测到邻苯二甲酸酯,国外已称它们为“第二个全球性的PCB污染物”。
     地下水是人类赖以生存的水资源的重要组成部分,我国有2/3的人口以地下水为饮用水源,地下水污染及其防治问题已引起了世界各国政府与公众的关注。本论文针对江汉平原地下水及浅层含水层沉积物中邻苯二甲酸酯的分布特征研究,筛选出检出率及含量均较高的五种邻苯二甲酸酯[邻苯二甲酸二甲酯(DMP)、邻苯二甲酸二乙酯(DEP)、邻苯二甲酸二正丁酯(DBP)、邻苯二甲酸二异丁酯(DIBP)、邻苯二甲酸二乙基己基酯(DEHP)]作为研究对象,对其在浅层含水层沉积物中的吸附行为进行研究。
     论文取得了以下成果:
     一、主要介绍了环境内分泌干扰物质和邻苯二甲酸酯类化合物的理化性质、危害、污染现状,综述了近年来国内外邻苯二甲酸酯类化合物分析测试方法和邻苯二甲酸酯类物质在各种吸附材料中吸附行为的研究进展。
     二、选用江汉平原地区浅层含水层沉积物作为吸附剂,利用反相高效液相色谱技术对筛选出的五种PAEs(DMP、DEP、DBP、DIBP、DEHP)进行吸附动力学研究。结果表明,经四种动力学模型对吸附过程进行拟合,抛物线方程最优,其相关系数(R值)最大,说明吸附过程受到扩散机制的制约。
     采用批次吸附实验方法研究了五种PAEs在浅层含水层沉积物上共存的等温吸附行为,在六种浅层含水层沉积物中PAEs的吸附能较好地符合线性吸附规律,在此六种吸附质中PAEs吸附线性拟合的相关性系数均值在0.6744~0.8833之间,且对于同一浅层含水层沉积物中所得参数Kd(沉积物-水分配系数)基本符合:DEP     动态土柱法进行阻滞因子的计算,实验进行100天,只有DMP和DEP穿透,因此只能求出DMP和DEP的阻滞因子。结果表明当地下水迁移10000m时,邻苯二甲酸二甲酯只迁移了65m;当地下水迁移10000m时,邻苯二甲酸二乙酯迁移了55m。
     三、分别考察了不同的pH值和不同离子强度条件下五种邻苯二甲酸酯混合溶液在一种浅层含水层沉积物WCD32中的吸附影响。结果显示在溶液中加酸或加碱条件会增加PAEs的吸附量。pH值为3时,DIBP的吸附量明显增加,且DEHP的吸附速率加快,其余PAEs的吸附量所受影响不明显;在碱性条件下,DMP、DEP、DBP、DIBP的吸附量均明显增加,且碱性越强吸附量越大,由于各条件下DEHP均被完全吸附,所以我们无法得知pH对其吸附量的影响,但是其吸附速率随pH增加有所减慢。通过分析吸附后邻苯二甲酸酯在液相色谱测试时的谱图,发现碱性条件下,有新的峰出现,且根据目测新生成的峰面积随pH值增大而增加,这一规律与吸附量的增加规律比较符合。
     吸附过程中NaCl的存在使得邻苯二甲酸酯的吸附量增加,但是随着NaCl浓度的变化,吸附量的增加趋势会发生变化:NaCl的存在会增加邻苯二甲酸酯的吸附量,DEHP的吸附量随着其浓度增加而增加,且增加趋势较其他四种邻苯二甲酸酯大;DMP、DIBP、DBP在一定NaCl浓度范围内(浓度为0.0015N、0.003N、0.015N)吸附量随其浓度增加而增加,即在此浓度范围内NaCl会促进其吸附;在NaCl浓度达到0.03这三种PAEs的吸附量反而比0.015N时少,即在在NaCl浓度达到0.015N-0.03N的某一值时对邻苯二甲酸酯吸附的促进作用会减小。
Environmental hormone is a class of chemical compounds in environment. It may affect human and animal on their normal endocrines, leading to reproductive, developmental and behavioral disorder. For Environmental hormone are harmful to human beings and animals, the research of EDCs is worldwide concerned.
     Phthalic acid esters (PAEs) are an important group of environment hormones. Their main application is as plasticizers in the manufacture of plastics. In recent years, large amount of plastic acid esters have caused a wide distributions in the world. It can enter human body through breathing, diet and skin. Because there is not chemical bond exist between PAEs and Plastic products. They just joined together with the hydrogen key and vander Waals force. It will be dissolved out in suitable organic solvent and cause pollution to the environment, living beings and food. they have been found in sediments, natural waters, soils, aquatic organism and ground waters, PAEs have become one of the most prevalent contaminants or the second PCBs pollutants.
     Groundwater is an important part resource in China for the survival of human, two thirds of the population are living with groundwater for drinking water, groundwater pollution and its prevention have attracted the world's governments' and the public's attention. This thesis aims at the study of characteristics of PAEs in Jianghan plain water and sediment, we studied sorption behavior of five PAEs on Shallow aquifer sediment, including DMP、DEP、DBP、DIBP and DEHP, which have high contents and detection rates.
     This thesis about the study of sorption of 5 PAEs on shallow aquifer sediment are as follows:
     1. Chapter one introduced the physiological function, existence manner, harm and analytical methods of phthalatic acid esters, summarized the recent advance of analysis method of PAEs in the world and the sorption study on some adsorption materials.
     2. Adsorption kinetics and adsorption isotherms of DMP, DEP, DBP, DIBP and DEHP on the shallow aquifer sediment of Jianghan Plain were studied with reverse-phase high performance liquid chromatography. Results showed that parabolic equation has the best correlation coefficient, it means that the adsorption process is restricted by the diffusion mechanism.
     The results of the study of batch sorption experiment showed that the adsorption isotherms of five PAEs on shallow aquifer sediment are well fitted linear model.The correlation coefficient of 5 PAEs on 6 shallow aquifer sediment between 0.6744 and 0.8822, Kd (sediment and water distribution coefficient) on the same shallow aquifer sediment are as follows: DEP     We used dynamic soil column method to calculate retardation factor, only DMP and DEP can breakthrough. The results showed that when the groundwater transfer 10000m, DMP will move 65m, However, DEP will move 55m.
     3. Influence of pH and ionic strength on adsorption behavior was investigated on shallow aquifer sediment WCD32. It can be found that after adding acid or alkali, the adsorption amounts of PAEs increase. pH=3, the adsorption amounts of DIBP increase obviously, the adsorption rate of DEHP quicken, DMP、DEP and DBP don't change a lot. When pH=7 and pH=9, the adsorption amounts of DMP、DEP、DBP、DIBP increase sharply, however, pH=9 have more increased amounts. After the analysis of the spectra tested with liquid chromatographic after adsorption, we found there were some new peaks appeared, when pH=9, the areas of peaks were larger more than pH=7.
     The existence of NaCl in solution can increase the adsorption quantity of PAEs. the adsorption quantity of DEHP increased with the concentration of NaCl in solution, increasing amount was much more than others. the adsorption quantity of DMP、DIBP、DBP increased on certain concentration range of NaCl, When the contents of NaCl was 0.0015N、0.003N、0.015N, the adsorption quantity increased with the concentration of NaCl, When the concentration of NaCl was 0.03 N, the adsorption quantity of DMP、DIBP、DBP were less than 0.015N NaCl in solution, It showed that When the contents of NaCl between 0.015N~0.03N, the role of NaCl in promoting of the sorption of PAEs will decrease.
引文
[1]丁小东,朱明华.环境激素污染研究[J].能源环境保护,2006,20(004):13-15.
    [2]Hutchinson T, Matthiessen P. Endocrine disruption in wildlife:identification and ecological relevance[J]. Science of the Total Environment,1999,233(1):220.
    [3]Colborn T, vom Saal F, Soto A. Developmental effects of endocrine-disrupting chemicals in wildlife and humans[J]. Environmental Impact Assessment Review,1994,14(5-6):469-489.
    [4]Key S. New study highlights hazards on hormone disrupting chemicals[J]. World Disease (weekly Plus),1998,911-12.
    [5]Sharpe R, Skakkebaek N. Are oestrogens involved in falling sperm counts and disorders of the male reproductive tract?[J]. The Lancet,1993,341(8857):1392-1396.
    [6]Allen Y, Matthiessen P, Scott A, Haworth S, Feist S, Thain J. The extent of oestrogenic contamination in the UK estuarine and marine environments--further surveys of flounder[J]. The Science of the Total Environment,1999,233(1-3):5-20.
    [7]Hutchinson T, Pounds N, Hampel M, Williams T. Impact of natural and synthetic steroids on the survival, development and reproduction of marine copepods (Tisbe battagliai)[J]. The Science of the Total Environment,1999,233(1-3):167-179.
    [8]Colborn T, Saal A. vom and Soto, AM 1993. Developmental effects of endocrine disrupting chemicals in wildlife and human[J]. Environmental Health Perspectives,101(5):378-384.
    [9]曹信孚.日试验证实低浓度壬基苯酚的环境激素作用[J].广州环境科学,2002,17(002):24-24.
    [10]齐文启,孙宗光.痕量有机物的监测.北京:化学工业出版社,2001.
    [11]Gillesby B, Zacharewski T. Exoestrogens:mechanisms of action and strategies for identification and assessment[J]. Environmental Toxicology and Chemistry,1998,17(1):3-14.
    [12]江田汉,赖玉平.环境激素问题浅析[J].中国环境管理,2001,(001):43-45.
    [13]孔昌俊.环境激素对人类健康的影响[J].辽宁城乡环境科技,2000,20(006):1-4.
    [14]程萍,彭秀丽.环境激素与人类健康[J].郑州铁路职业技术学院学报,2006,18(003):40-42.
    [15]赵泽文,常青,梁志清.环境雌激素对健康的影响[J].中国临床康复,2004,8(009):1724-1725.
    [16]Kawauchi H, Suzuki K, Yamazaki T, Moriyama S, Nozaki M, Yamaguchi K, Takahashi A, Youson J, Sower S. Identification of growth hormone in the sea lamprey, an extant representative of a group of the most ancient vertebrates[J]. Endocrinology,2002,143(12):4916.
    [17]Baker M. Evolution of regulation of steroid-mediated intercellular communication in vertebrates: insights from flavonoids, signals that mediate plant-rhizobia symbiosis[J]. Journal of Steroid Biochemistry and Molecular Biology,1992,41(3-8):301-308.
    [18]Porter W, Green S, Debbink N, Carlson I. Groundwater pesticides:interactive effects of low concentrations of carbamates aldicarb and methomyl and the triazine metribuzin on thyroxine and somatotropin levels in white rats[J]. Journal of Toxicology and Environmental Health, Part A, 1993,40(1):15-34.
    [19]Power M. The effect of reduction in numbers of ommatidia upon the brain of Drosophila melanogaster[J]. Journal of Experimental Zoology,2005,94(1):33-71.
    [20]Shen K, Novak R. DDT Stimulates c-erbB2, c-met, and STATS Tyrosine Phosphorylation, Grb2-Sos Association, MAPK Phosphorylation, and Proliferation of Human Breast Epithelial Cells* 1[J]. Biochemical and Biophysical Research Communications,1997,231(1):17-21.
    [21]Gomez-Hens A, Aguilar-Caballos M. Social and economic interest in the control of phthalic acid esters[J]. TrAC Trends in Analytical Chemistry,2003,22(11):847-857.
    [22]叶常明.环境中的领苯二甲酸酯[J].环境科学进展,1993,1(002):36-47.
    [23]Stales C, Peterson D, Parkerton T, Adams W. The environmental fate of phthalate esters:a literature review[J]. Chemosphere,1997,35(4):667-749.
    [24]Howard P. S. Banerjee and KA Robillard.1985. Measurement of water solubilities, octanol/water partition coefficients, and vapor pressures of commercial phthalate esters[J]. Environ Toxicol Chem,4653-661.
    [25]Staples C, Parkerton T, Peterson D. A risk assessment of selected phthalate esters in North American and Western European surface waters[J]. Chemosphere,2000,40(8):885-891.
    [26]孙胜龙.环境激素与人类未来[M].化学工业出版社,2005.
    [27]周文敏,寇洪如,王湘君.环境优先污染物[J].北京:中国环境科学出版社,1989,13-14.
    [28]Carlsen E, Giwercman A, Keiding N, Skakkebaek N. Evidence for decreasing quality of semen during past 50 years[J]. British Medical Journal,1992,305(6854):609.
    [29]Calafat A, Brock J, Silva M, Gray L. Urinary and amniotic fluid levels of phthalate monoesters in rats after the oral administration of di (2-ethylhexyl) phthalate and di-n-butyl phthalate[J]. Toxicology,2006,217(1):22-30.
    [30]Koch H, Bolt H, Preuss R, Angerer J. New metabolites of di (2-ethylhexyl) phthalate (DEHP) in human urine and serum after single oral doses of deuterium-labelled DEHP[J]. Archives of toxicology,2005,79(7):367-376.
    [31]Latini G, Del Vecchio A, Massaro M, Verrotti A, De Felice C. Phthalate exposure and male infertility [J]. Toxicology,2006,226(2-3):90-98.
    [32]Silva M, Kato K, Gray E, Wolf C, Needham L, Calafat A. Urinary metabolites of di-n-octyl phthalate in rats[J]. Toxicology,2005,210(2-3):123-133.
    [33]Foster P, Cattley R, Mylchreest E. Effects of di-n-butyl phthalate (DBP) on male reproductive development in the rat:implications for human risk assessment[J]. Food and Chemical Toxicology,2000,38S97-S99.
    [34]李文兰,季宇彬,杨波,吕东阳,姜安玺.环境中邻苯二甲酸丁苄酯的雌激素生物活性[J]. 城市环境与城市生态,2003,16(001):22-24.
    [35]Saillenfait A, Payan J, Fabry J, Beydon D, Langonne I, Gallissot F, Sabate J. Assessment of the developmental toxicity, metabolism, and placental transfer of di-n-butyl phthalate administered to pregnant rats[J]. Toxicological Sciences,1998,45(2):212.
    [36]Ema M, Miyawaki E. Effects on development of the reproductive system in male offspring of rats given butyl benzyl phthalate during late pregnancy[J]. Reproductive Toxicology,2002, 16(1):71-76.
    [37]齐文启,孙宗光.痕量有机污染物的监测[M].化学工业出版社:环境科学与工程出版中心,2001.
    [38]黄骏雄.样品制备与处理的进展——无溶剂萃取技术[J].化学进展,1997,9(002):179-191.
    [39]庞金梅,池宝亮.苯二甲酸酯的微生物降解与转化[J].环境科学,1994,15(003):88-90.
    [40]Jen J, Liu T. Determination of phthalate esters from food-contacted materials by on-line microdialysis and liquid chromatography[J]. Journal of Chromatography A,2006,1130(1):28-33.
    [41]Atlas E, Giam C. Global transport of organic pollutants:ambient concentrations in the remote marine atmosphere[J]. Science,1981,211(4478):163.
    [42]Cautreels W, Van Cauwenberghe L. Comparison between the organic fraction of suspended matter at a background and an urban station[J]. The Science of the Total Environment,1977, 8(1):79-88.
    [43]沈婷.室内空气和降尘中邻苯二甲酸酯的分析研究[D].北京工业大学,2009.
    [44]Sha F. Distribution of Phthalic Acid Esters in Wuhan section of the Yangtze River, China[J]. Journal of hazardous materials,2008,154(1-3).
    [45]王程,刘慧,蔡鹤生,梁颖,梁合诚,熊启华.武汉市地下水中酞酸酯污染物检测及来源分析[J].环境科学与技术,2009,32(010):118-123.
    [46]Zeng F, Cui K, Xie Z, Wu L, Liu M, Sun G, Lin Y, Luo D, Zeng Z. Phthalate esters (PAEs): emerging organic contaminants in agricultural soils in peri-urban areas around Guangzhou, China[J]. Environmental Pollution,2008,156(2):425-434.
    [47]Liu H, Liang H, Liang Y, Zhang D, Wang C, Cai H, Shvartsev S. Distribution of phthalate esters in alluvial sediment:A case study at JiangHan Plain, Central China[J]. Chemosphere,2010, 78(4):382-388.
    [48]莫测辉,蔡全英.我国城市污泥中邻苯二甲酸酯的研究[J].中国环境科学,2001,21(004):362-366.
    [49]Aranda J, O'connor G, Eiceman G. Effects of sewage sludge on di-(2-ethylhexyl) phthalate uptake by plants[J]. Journal of Environmental Quality,1989,18(1):45.
    [50]Ruminski J, Dejewska B, Wojtanis J. Environmental Research. Part Ⅰ. Investigations on Dioctyl Phthalate (DEHP) Pollution in Soil and Surface Water near Wabrzezno Torun District)[J]. POLISH JOURNAL OF ENVIRONMENTAL STUDIES,1995,465-69.
    [51]Marcilla A, Garcia S, Garcia-Quesada J. Migrability of PVC plasticizers[J]. Polymer Testing, 2008,27(2):221-233.
    [52]Borden R, Gomez C, Becker M. Geochemical indicators of natural bioremediation[J]. Ground Water,1995,33180-189.
    [53]王焰新.地下水污染与防治.武汉:中国地质大学出版社,2002.
    [54]李纯,武强.地下水有机污染的研究进展[J].工程勘察,2007,(001):27-30.
    [55]Kluwe W, McConnell E, Huff J, Haseman J, Douglas J, Hartwell W. Carcinogenicity testing of phthalate esters and related compounds by the National Toxicology Program and the National Cancer Institute[J]. Environmental Health Perspectives,1982,45129.
    [56]Charles A, Dennis R, Thomas F. The environmental fate of phthalate esters:a literature review[J]. Chemosphere,1997,35(4):667-749.
    [57]Foster P, Mylchreest E, Gaido K, Sar M. Effects of phthalate esters on the developing reproductive tract of male rats[J]. Human reproduction update,2001,7(3):231.
    [58]曾锋,陈丽旋,崔昆燕,张干.硅胶-氧化铝层析柱-气相色谱法测定沉积物中邻苯二甲酸酯类有机物[J].分析化学,2005,33(008):1063-1067.
    [59]Wang C, Liang Y, Zhang D, Liu H, Xiong Q. Optimizing determination of trace phthalate esters in groundwater by solid phase extraction-gas chromatography[J].
    [60]Mabey W, Smith J, Podoll R, Johnson H, Mill T, Chou T, Gates J, Partridge I, Jaber H, Vandenberg D. Aquatic fate process data for organic priority pollutants [J]. US Environmental Protection Agency, Office of Water Regulations and Standards, Washington, DC EPA,1982, 4404-81.
    [61]郑和辉,赵立文,刘玉敏,周香玉,韩志宇.饮用水中邻苯二甲酸酯的气相色谱-质谱测定法[J].环境与健康杂志,2005,22(005):377-378.
    [62]Brossa L, Marce R, Borrull F, Pocurull E. Application of on-line solid-phase extraction-gas chromatography-mass spectrometry to the determination of endocrine disruptors in water samples[J]. Journal of Chromatography A,2002,963(1-2):287-294.
    [63]Penalver A, Pocurull E, Borrull F, Marce R. Determination of phthalate esters in water samples by solid-phase microextraction and gas chromatography with mass spectrometric detection[J]. Journal of Chromatography A,2000,872(1-2):191-201.
    [64]Cai Y, Jiang G, Liu J, Zhou Q. Multi-walled carbon nanotubes packed cartridge for the solid-phase extraction of several phthalate esters from water samples and their determination by high performance liquid chromatography [J]. Analytica Chimica Acta,2003,494(1-2):149-156.
    [65]Orsi D, Gagliardi L, Porr R, Berri S, Chimenti P, Granese A, Carpani I, Tonelli D. A environmentally friendly reversed-phase liquid chromatography method for phthalates determination in nail cosmetics[J]. Analytica Chimica Acta,2006,555(2):238-241.
    [66]Di Toro D, Zarba C, Hansen D, Berry W, Swartz R, Cowan C, Pavlou S, Allen H, Thomas N, Paquin P. Technical basis for establishing sediment quality criteria for nonionic organic chemicals using equilibrium partitioning[J]. Environmental Toxicology and Chemistry,2009, 10(12):1541-1583.
    [67]Wang X, Grady Jr C. Comparison of biosorption isotherms for di-n-butyl phthalate by live and dead bacteria[J]. Water Research,1994,28(5):1247-1251.
    [68]李立忠,刘子元,孙杰.土壤对酞酸酯类化合物(PAES)的吸附作用[J].中南民族大学学报:自然科学版,2006,25(001):15-17.
    [69]Chen C, Chen C, Chung Y. Removal of phthalate esters by [alpha]-cyclodextrin-linked chitosan bead[J]. Bioresource technology,2007,98(13):2578-2583.
    [70]郭宏栋,周敏,童丹,陈慧.邻苯二甲酸酯在黄河沉积物上的吸附特性[J].环境科学与技术,2009,32(001):6-9.
    [71]迟杰,康江丽.水体中悬浮颗粒物对酞酸酯的吸附和解吸特性[J].环境化学,2006,25(004):405-408.
    [72]Venkata Mohan S, Shailaja S, Rama Krishna M, Sarma P. Adsorptive removal of phthalate ester (Di-ethyl phthalate) from aqueous phase by activated carbon:A kinetic study[J]. Journal of hazardous materials,2007,146(1-2):278-282.
    [73]黄荣新.酞酸酯类激素在污水厂的迁移及GAC吸附与生物降解研究[D].哈尔滨工业大学,2007.
    [74]Cousins I, Mackay D. Correlating the physical-chemical properties of phthalate esters using the [] three solubility'approach[J]. Chemosphere,2000,41(9):1389-1399.
    [75]Ellington J. Octanol/Water Partition Coefficients and Water Solubilities of Phthalate Esters[J]. J Chem Eng Data,1999,44(6):1414-1418.
    [76]奚旦立.环境监测[M].高等教育出版社,1987.
    [77]Sparks D. Environmental soil chemistry[M]. Academic Pr,2003.
    [78]Havlin J, Westfall D, Olsen S. Mathematical models for potassium release kinetics in calcareous soils[J]. Soil Science Society of America Journal,1985,49(2):371.
    [79]Chien S, Clayton W. Application of Elovich equation to the kinetics of phosphate release and sorption in soils[J]. Soil Science Society of America Journal,1980,44(2):265.
    [80]Crank J. The mathematics of diffusion[M]. Oxford University Press, USA,1979.
    [81]Navarro A, Endo S, Gocht T, Barth J, Lacorte S, Barcelo D, Grathwohl P. Sorption of alkylphenols on Ebro River sediments:comparing isotherms with field observations in river water and sediments[J]. Environmental Pollution,2009,157(2):698-703.
    [82]赵雪松,胡小贞,卢少勇,金相灿,盛力.不同粒径方解石在不同pH值时对磷的等温吸附特征与吸附效果[J].环境科学学报,2008,28(009):1872-1877.
    [83]ElShafei G, Nasr I, Hassan A, Mohammad S. Kinetics and thermodynamics of adsorption of cadusafos on soils[J]. Journal of hazardous materials,2009.
    [84]刘辉,方战强,陈晓蕾,曾宝强.活性炭吸附去除水中邻苯二甲酸二丁酯的动力学研究[J].净水技术,2008,27(002):23-26.

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700