西安市公园大气降尘中Cu、Pb、Zn、Ni、Cd的化学形态特征及其生物有效性
CHEMICAL SPECIES AND BIOAVAILABILITY OF Cu, Pb, Zn, Ni AND Cd OF DUSTFALL FROM XI'AN PARKS IN CHINA
-
摘要: 采用连续提取法和原子吸收光谱法测定了西安市11个公园降尘中Cu、Pb、Zn、Ni、Cd等元素化学形态的含量,结果表明,各公园降尘中Cu和Pb含量均超过该市道路灰尘平均含量的7倍和3倍以上,有机态、铁锰氧化物态、碳酸盐态和可交换态分别为Cu总量的38%、31%、15%和13%;有机态、铁锰氧化态、碳酸盐态和交换态分别为Pb总量的35%、29%、14%和14%;除北郊的公园外,其它公园降尘中Zn的含量与道路灰尘接近,Zn以铁锰氧化态或残渣态为主;Cd含量均未超过道路灰尘中的平均含量;除城市运动公园外,其它公园降尘中Ni含量低于或接近陕西省塿土.有机结合态Cu和Pb主要与生物碎屑物质和化石燃料不完全燃烧的产物有关,铁锰氧化物结合态和交换态与制造业排放有关,碳酸盐结合态与表土扬尘有关.Ni和Cd以残渣态为主.各公园降尘中的Pb和Cu对人体健康具有潜在的威胁.Abstract: Chemical speciation of Cu, Pb, Zn, Ni and Cd in dustfall samples from 11 parks in Xi'an City was extracted extracted by using the Tessier's method and analyzed by Atomic Absorption Spectrophotometry (AAS). The study shows that the contentrations of Cu and Pb in the dustfall samples exceed their respective averages of Cu and Pb in the urban dusts by 7 and 3 times, while the contents of Cd are of the same orders of the average of the road dusts. Contentrations of Zn in the samples collected in the northern parks are two times larger than those collected in the southern and eastern parks. The latter is the almost same order as averaged concentration of Zn in the urban dusts. Contentrations of Ni in the dustfall samples from these parks are very low and lower than or close to those in Lou Soil in Shaan'xi province. The average proportion of Cu bound to organic matter, bound to Fe-Mn oxides, bound to carbonates and exchangeable form is 38%, 31%, 15% and 13% respectively while the average value of Pb bound to organic matter, bound to Fe-Mn oxides, bound to carbonates and the exchangeable one is 35%, 29%, 14% and 14% respectively. Cu and Pb bound to organic matter could be attribated to biological wastes and production of incomplete combustion of fossil fuel, while the elements bound to Fe-Mn oxides and exchangeable ones could be considered as emissions of manufacturing industries and elements bound to carbonates are likely from aeolian dusts. Ni and Cd bound to residual speciation contribute to 65% and 85% of their total amounts respectively. The bioavailability estimated from chemical species of Cu, Pb, Zn, Ni and Cd in the dustfall samples collected in the parks indicate that only Cu and Pb can potentially threaten human health.
-
Key words:
- dustfall /
- chemical speciation /
- heavy metals /
- bioavailability /
- pollutant sources
-
-
[1] Purves D. Contamination of urban garden soils with copper, boron [J]. Nature, 1966, 210, 1077-1078 [2] Lantzy R T, Maikenzie F T. Atmospheric trace metals: global cycles and assessment of man's impact [J]. Geochimica et Cosmochimica Acta, 1979, 43 (4): 511-525 [3] Nriagu J O, Pacyna J M. Quantitative assessment of worldwide contamination of air, water and soils by trace elements [J]. Nature, 1988, 333(12): 134-139 [4] Wong C S C, Li X D, Zhang G, et al. Atmospheric deposition of heavy metals in the Pearl River Delta, China [J]. Atmospheric Environment, 2003, 37: 767-776 [5] Han Y M, Du P X,Cao J J, et al. Multivariate analysis of heavy metal contamination in urban dust s of Xi'an, Central China [J]. The Science of t he Total Environment, 2006, 355: 176-186 [6] 冯茜丹, 党志, 黄伟林. 广州市秋季PM2.5中重金属的污染水平与化学形态分析 [J]. 环境科学, 2008, 29(3): 569-575 [7] 任伟琴, 梅凡民, 陈敏. 西安灌区土壤重金属形态特征及生态风险评价 [J]. 环境化学, 2009, 28(3): 451-452 [8] 田晖. 西安市街道灰尘中铬、镉、铅赋存状态及环境效应 [J]. 北京地质, 2002,14(2): 34-39 [9] Zhang X Y,Cao J J, Li L M, et al. Characterization of atmospheric aerosol over Xian in the South Margin of the Loess Plateau, China [J]. Atmospheric Environment, 2002, 36: 4189-4199 [10] 高连存, 冯素萍, 何桂华, 等. 模拟酸雨条件下降尘中Cu, Pb, Zn, Cr各形态的溶出和转化研究 [J]. 环境化学, 1994,13(5): 448-451 [11] 周琳, 曾英, 倪师军. 成都经济生态区大气降尘中镉赋存形态的研究 [J]. 上海环境研究, 2006, 25(4): 144-146 [12] 姜伟. 重庆主城降尘中六种金属及其化学形态研究 . 西南大学硕士学位论文, 2008: 20-24 [13] 赵兴敏, 赵蓝坡, 花修艺. 长春市大气降尘中重金属的分布特征和来源分析 [J]. 城市环境与城市生态, 2009, 22(4): 30-32 [14] 赵锁志, 王沛东, 包凤琴,等. 呼和浩特市大气降尘中镉赋存形态分析 [J]. 岩矿测试, 2009, 28(4):329-332 [15] Tessier A, Campbell P G C, Bission M. Sequential extraction procedure for the speciation of particulate trace metals [J]. Analysis Chemistry, 1979, 51(7): 844-851 [16] 郭水良, 黄朝表. 金华市郊杂草对土壤重金属元素的吸收与富集作用(Ⅰ)——6种重金属元素在杂草和土壤中的含量分析 [J].上海交通大学学报: 农业科学版,2002,20(1):23-29 [17] 陈怀满. 环境土壤学[M]. 北京: 科学出版社, 2005: 236-237 [18] 卢瑛, 龚子同. 南京城市土壤中重金属的化学形态分布 [J].环境化学, 2003, 22(2):131-136 [19] 文启忠. 黄土地球化学[M]. 北京: 科学出版社, 1989: 115-118 [20] 倪刘建, 张甘霖, 阮心玲,等. 南京市不同功能区大气降尘的沉降通量及污染特征 [J]. 中国环境科学, 2007,27(1): 2-6 [21] 高瑞英, 郭璇华. 应用ICP-MSS测定大气降尘中有毒重金属的化学形态 [J]. 广东化工, 2005, 32(5): 4-7 [22] 国家技术监督局,中华人民共和国国家标准. 车用无铅汽油标准 GB 17930—1999[S].北京:中国标准出版社,2000 [23] 黄进. 重庆市主要农地土壤镉铅区域分布、环境容量及对酸雨的响应 . 西南农业大学博士学位论文, 2002, I-II
[24] 夏增禄, 李森照, 李廷芳, 等. 土壤元素背景值及其研究方法 [M]. 北京: 气象出版社, 1987, 320-321 [25] 陆晓华, 曾汉才, 欧阳中华. 燃煤电厂排放细微灰粒中痕量元素的分布与富集规律 [J]. 环境化学, 1995, 14(6):489-493 [26] Steinnes E, Allen R O. Petersen H M, et al. Evidence of large scale heavy-metal contamination of natural surface soils in Norway from long-range atmospheric transport [J]. The Science of the Total Environment, 1997, 20(5): 255-206 [27] Ratha D S, Sahu B K. Source and distribution of metals in urban soil of Bombay, India, using multivariate statistic-cal techniques [J]. Environmental Geology, 1993, 22: 276-285 [28] 雒昆利, 苏文质, 杨建业, 等. 西安市区降尘的元素特征 [J]. 西安矿业学院学报, 1996, 16(1): 41-44 -

计量
- 文章访问数: 1043
- HTML全文浏览数: 981
- PDF下载数: 440
- 施引文献: 0