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1.
采用固相微萃取-气质联用技术对珠江三角洲9个城市共48个湖库水体中的土臭素(GSM)、2-甲基异茨醇(MIB)和2,3,6-三氯苯甲醚(TCA)等5种嗅味物质进行检测,并探讨污水处理厂和自来水厂处理工艺中嗅味物质的浓度变化规律,同时研究强化混凝沉淀工艺对嗅味物质的去除效果.结果表明:珠江三角洲湖库水体中嗅味问题最严重的是广州、佛山、肇庆、东莞、惠州和深圳6个城市,各市湖库的嗅味物质平均浓度为70.93~116.61 ng/L;中山、珠海与江门3个城市的嗅味问题不明显,各市湖库的嗅味物质平均浓度为22.78~58.82 ng/L;珠江三角洲的湖库中浓度最高的嗅味物质是MIB、TCA和GSM,这3种嗅味物质占了嗅味物质总浓度的80.18%~100.00%;污水处理厂和自来水厂中的处理工艺对嗅味物质均有一定的去除效果,嗅味物质的去除主要发生在混凝沉淀阶段;污水处理厂对MIB、TCA和GSM的平均去除率分别为53.55%、57.40%和72.90%;自来水厂对MIB、TCA和GSM的平均去除率分别为64.14%、69.63%和36.86%;强化混凝沉淀实验中,当嗅味物质初始浓度为200 ng/L时,Al2O3投加量为13.75 mg/L可使得混凝沉淀工艺对嗅味物质的去除效果最佳且保证铝盐不超标,嗅味物质浓度增大时Al2O3投加量也需增大;反应体系的pH值处于5~8时,混凝沉淀工艺对嗅味物质的去除效果最佳;混凝搅拌速率越快,嗅味物质的去除率越高且越快达到稳定.  相似文献   

2.
若干水华相关藻类对太湖水体异味物质贡献的初步研究   总被引:1,自引:0,他引:1  
太湖水体中嗅味物质2-甲基异莰醇(MIB)和土臭素(Geo)的出现与水华发生在时间上高度重叠,为探寻水华中常见藻类与嗅味的关系,本研究通过对实验室培养藻株和野外水样比较分析,探寻了部分藻株与太湖水体嗅味物质的关系.分析实验室培养的15株蓝藻(其中11株微囊藻)、4株绿藻和4株硅藻,仅硅藻培养物测定出了Geo,所有藻株均未检测出MIB;对太湖典型水样分析结果显示,水体中MIB与Geo的浓度与微囊藻细胞浓度无相关性;实验室模拟微囊藻水华腐败结果显示,无论是好氧还是厌氧条件下均未产生MIB和Geo;这些数据结果说明湖水中MIB和Geo与水华主要种群微囊藻无直接关系.在鱼腥藻水华中测出了高浓度的MIB,周年水样分析结果显示鱼腥藻细胞数与MIB浓度变化规律一致,因此鱼腥藻可能是MIB的重要来源.但实验室培养的Anabaena sp.PCC7120无论是在缺氮还是有氮培养条件下均不产MIB和Geo,说明嗅味物质的产生具有藻株特异性.  相似文献   

3.
2006-2015年内蒙古呼伦湖富营养化趋势及分析   总被引:4,自引:1,他引:3  
以内蒙古呼伦湖为研究对象,20062015年水质数据为基础,分析呼伦湖的富营养化变化趋势及其影响因素.结果表明,20062015年呼伦湖各水质指标都有不同程度的变幅,其中盐度变化范围为0.75~1.71 ng/L,均值为1.32 ng/L,2010年达到峰值1.71 ng/L,随后呈现逐年递减趋势;pH的变化范围为8.78~9.40,水体偏碱性;透明度的变化范围为0.17~0.26 m,近三年来透明度持续下降;溶解氧浓度变化范围为4.05~10.62 mg/L,均值为7.12 mg/L.总氮浓度的变化范围为1.16~3.53 mg/L,总磷浓度的变化范围为0.13~0.25 mg/L,叶绿素a浓度的变化范围为3.31~10.36 mg/m3,N/P比变化范围为4.92~15.35,水质已经达到地表水环境质量Ⅳ~Ⅴ类水体标准,是磷限制性湖泊.利用综合营养状态指数法对呼伦湖水体富营养化进行评价,2006-2015年呼伦湖水体表现出中度—重度—中度—轻度的变化趋势.通过分析呼伦湖富营养化的影响因素,结果表明,影响呼伦湖富营养化的可能因素为外源输入和入湖径流量,同时水深和水温也是呼伦湖发生富营养化的驱动因素,pH、透明度和溶解氧是呼伦湖富营养化影响水质的最主要表现指标.  相似文献   

4.
合肥塘西河异味物质及异味影响因子研究   总被引:2,自引:0,他引:2       下载免费PDF全文
以合肥市塘西河为研究对象,2014-2015年逐月对其水体水质和异味物质进行监测,同时结合塘西河浮游植物群落结构调查,综合分析塘西河异味物质变化规律及其影响因素.研究发现,塘西河异味暴发集中发生在夏季,夏季二甲基异莰醇浓度可达4909 ng/L,土腥素浓度可达197 ng/L.浮游植物群落结构调查表明,秋、冬季塘西河优势种类为蓝藻,春、夏季为硅藻、绿藻或隐藻.主成分分析得到5种主成分分别解释了光照、有机质、微生物活动、氮、磷等对水质的影响.相关性分析结果表明,氮是塘西河异味的限制因素,水体中氮浓度较高是异味产生的重要原因.  相似文献   

5.
轮虫是水体中重要的浮游生物类群,对环境变化敏感,是水生态系统中食物链及微型食物网的关键环节.于2015年夏季(7月)和冬季(12月)对养殖池塘、水库、广州城市湖泊、珠江河口及珠江河段水域的轮虫和理化环境指标进行了调查分析,共发现轮虫26属、76种,其中裂痕龟纹轮虫(Anuraeopsis fissa)在7月河流水体占绝对优势,但12月数量明显减少.冬季珠江河段和河口水体群落多样性指数与均匀度指数较夏季高,群落结构较夏季稳定.调查水体轮虫丰度范围为33~2625 ind./L,城市湖泊夏季丰度较高,冬季有所下降,而养殖池塘轮虫丰度在冬季有所上升.群落结构相似性分析(ANOSIM)分析表明,不同类型水体之间差异显著,尤以湖泊与河流差异性最大,广布多肢轮虫(Polyarthra vulgaris)在湖泊贡献率最高,暗小异尾轮虫(Trichocerca pusilla)其次;裂痕龟纹轮虫在河流贡献率最高,优势种丰度差异是造成湖泊与河流群落结构差异的主要原因.统计分析表明,轮虫丰度与叶绿素a浓度呈正相关.冗余分析与ANOSIM分析发现广布多肢轮虫在流花湖等叶绿素a浓度较高的静态水体中易形成优势;裂痕龟纹轮虫和角突臂尾轮虫(Brachionus angularis)在珠江河段等总氮和总磷浓度高的富营养化流动水体中易形成优势.综合轮虫群落结构和水质特征,广州市水体富营养化严重,耐污性轮虫种类多,应加强城市水生态系统保护和管理.  相似文献   

6.
底泥覆盖对浅水湖泊藻源性湖泛的控制模拟   总被引:1,自引:1,他引:0  
湖泛的发生与湖泊底部氧化还原条件和致黑致臭物充足供给直接相关.利用黄土和细沙对太湖湖泛易发区(月亮湾)底泥进行覆盖,模拟在湖泛可形成条件下,底泥-水体系及其界面主要物化性质与感官变化过程.结果表明:0.5 cm黄土和1.0 cm细沙的覆盖,从水色和嗅味半定量角度达到了对湖泛黑臭的控制,与对照组相比,覆盖组底泥间隙水中主要致黑物Fe2+浓度仅为对照组的1/3,主要致臭物甲硫醇和二甲基三硫醚等浓度则不到50%.进一步分析底部水体和底泥性质发现:经覆盖处理底部水体的溶解氧浓度提高近1倍,氧化还原电位基本处于250 m V以上水平,覆盖层1 cm左右表层氧化还原电位和p H均远高于对照底泥.以黄土为主的底泥覆盖,主要因阻隔了下层底泥中物质迁移供给和对厌氧微生物参与的控制,以及黄土本身性质对湖底物化环境的影响等,在藻体大量聚集和死亡的水柱环境中,较好地阻止了致黑致臭物的形成,从而较有效控制湖泛的发生.  相似文献   

7.
湖北长湖富营养化状况及时空变化(2012-2013年)   总被引:4,自引:1,他引:3  
为评估长湖水体富营养化程度,2012-2013年分4个季度对全湖区20个采样点的物理、化学和生物要素进行监测,在评价水质现状的基础上采用综合营养状况指数法和浮游植物细胞丰度指数法综合评价水体营养状况,并应用典型相关分析(CCA)方法揭示水体富营养化状况与湖泊理化要素之间的典型相关性.结果显示:4个季节长湖全湖区的水质均处于地表水IV类~劣V类水标准;综合营养状态指数值在49.54~82.55之间,浮游植物细胞丰度在2.88×106~61.73×106cells/L之间,均显示其处于富营养化状态;长湖富营养化状况的分布呈现一定的时空差异性;CCA分析显示,长湖理化要素变量可解释68.6%的水体富营养化状况变量的变异,影响其富营养化状况的主要理化因素有水体总磷、总氮、溶解氧、亚硝态氮、硝态氮浓度,水深和沉积物总磷、总氮含量.长湖水体富营养化主要是由于外源的磷污染,其次是氮污染,富营养化最严重的夏、秋季浮游植物的生长主要受氮营养限制,而冬、春季则部分受磷营养限制,部分属于过渡类型.因此,建议大力削减围网/围栏养殖量,同时考虑结合水生植物栽种等生态工程建设措施以降低长湖水体发生严重富营养化的风险,并进一步改善长湖的水质现状.  相似文献   

8.
根据2009年6月到2010年5月太湖水样中溶解态和结合态异味化合物(2-甲基异茨醇(MIB)、土嗅素(GEO)、β-环柠檬醛、β-紫罗兰酮)的月间采样分析结果,综合考虑各种环境因子以及蓝藻种属,探讨了溶解态和结合态异味化合物之间的关系以及影响太湖中异味化合物的主要环境因子.结果表明溶解态MIB和结合态β-环柠檬醛、β-紫罗兰酮是研究期间湖水中的主要异味化合物,这些物质对于太湖水体发生异味具有较大贡献或较大潜在贡献.通过本文研究和对以往文献讨论推测,太湖中溶解态和结合态异味化合物相关关系较弱的原因可能是,异味化合物生产和释放速率的变化、微生物降解、光解、吸附和挥发等.同时发现微囊藻和叶绿素a与太湖异味化合物关系密切.蓝藻水华对于太湖异味化合物的发生具有重要影响,控制蓝藻水华发生的关键是控制或减缓太湖异味问题.  相似文献   

9.
乌梁素海水体汞的分布特征及污染风险评估   总被引:4,自引:2,他引:2  
于2011年1月采集乌梁素海表层水样,对湖水中重金属Hg含量进行分析.结合Hg的空间分布特征,利用单因子指数综合污染评价指数与健康风险评价模型对Hg污染程度与风险进行评估.结果表明,乌梁素海表层水体中Hg的平均浓度为1.04μg/L,所有监测点Hg的含量都超出地表水Ⅲ类标准和国家渔业用水标准,50%的监测点超出了地表水Ⅳ类标准.水体中Hg的分布模式与流域排污口位置、入湖口及水动力条件有一定关系,高值区域分布在入湖口相对集中的西北与东北部,湖泊南部与出口处的含量相对较低,处于中等水平.乌梁素海湖水中Hg的非致癌性污染物所致的健康危害风险度介于0.75×10-9~2.15×10-9a-1之间,Hg所致的健康危害风险度的贡献率在71.43%~92.44%之间,表明Hg污染水平与健康风险都较高,应该给予特别关注.  相似文献   

10.
湖泊富营养化导致沉水植被大面积衰退和群落逆向演替,诱发一系列次生环境问题,并严重影响到水域生态环境质量.为了从对植物表型生长与C-N代谢生理指标影响的角度深度揭示富营养化水体中沉水植被的致衰退机制,本文以我国长江中下游淡水湖泊常见沉水植物优势种群——苦草(Vallisneria natans)为研究对象,利用L_(16)(4~5)正交试验设计方法,实验模拟研究富营养化水体中低氧、高铵和低光3种重要因素对苦草生长与C-N代谢生理指标的胁迫影响特征.本试验设置了3因素4水平,分别为4个低光照强度(50%、40%、30%和20%自然光照)和4个高铵浓度水平(0.5、1、2和4 mg/L)以及4个低氧处理浓度(7.5、6.5、5.5和4 mg/L).结果显示:光照强度低于30%、溶解氧浓度低于5.5 mg/L时,植株生长与C代谢受阻严重,碳水化合物储存量降低;铵态氮1.0 mg/L时,苦草N代谢活跃,游离氨基酸(FAA)含量明显升高,可溶性糖(SC)/FAA比降低,淀粉呈降低趋势.研究表明富营养湖泊中苦草的衰退是多种因素综合作用的结果,低氧、高铵与低光均会对苦草的生长与C-N代谢产生不利影响;受损沉水植被在藻-草稳态转换的富营养化湖泊中应通过控制水体高铵浓度,严控低氧出现,及时提高水下照度或透明度(如控磷)来予以保护和科学管理;而在次生裸地且藻类占优势的富营养化水体中沉水植被的恢复与重建过程不仅要降低水体营养盐水平尤其是氨氮的水平,还应着重考虑如何有效提高水下光强与溶解氧浓度,并将如上环境因子控制在一定变幅范围内,且控制条件应原则上严于保护受损沉水植被所需的条件.  相似文献   

11.
珠江广州段水环境问题与保护对策   总被引:8,自引:1,他引:8  
江涛  黎坤  柯栋 《湖泊科学》2004,16(3):282-284
珠江广州河段是广州市的主要水体,其日趋严重的水污染所导致的水质性缺水,已成为制约广州市可持续发展的一个重要因素.本文通过珠江广州河段的水环境现状评价,分析了珠江广州河段水环境污染的成因,并依此提出了珠江广州河段水环境的保护对策,即加快生活污水处理系统建设,调整工业布局和结构,推行清洁生产,重视畜禽养殖业污水的治理,实施环境水利工程,加大监督和执法力度,加强宣传教育,提高全民节约用水和环保意识.  相似文献   

12.
为研究广州市湖泊水体中的防腐剂及其毒性,在广州市选择15个湖泊采集水样,采用液液萃取-气质联用法对湖泊水体中的对羟基苯甲酸甲酯、对羟基苯甲酸乙酯等5种防腐剂进行浓度检测和毒性分析.结果表明:广州市区内15个湖泊水体中均检出防腐剂,但其浓度略低于国外天然水体中的浓度,溶解相的防腐剂平均浓度为5.06 ng/L,颗粒相的平均浓度为0.78 ng/L;广州市区的湖泊水体中溶解相浓度最高的防腐剂为对羟基苯甲酸丁酯,占总量的30.45%,对羟基苯甲酸苯甲酯所占比例最小,占6.71%;以防腐剂对发光细菌光强的抑制强弱来表征其毒性的大小,对羟基苯甲酸苯甲酯的毒性最强,对广州市湖泊水体环境的影响最大.  相似文献   

13.
“十三五”时期,长江流域水环境质量改善明显,但湖泊水质和富营养化状况改善滞后. 长江中游作为我国淡水湖泊集中分布区域之一,部分湖泊存在水环境质量恶化和富营养化加重问题. 本文以长江中游区域国家开展监测的洪湖、斧头湖、梁子湖、大通湖、洞庭湖和鄱阳湖这6个典型湖泊为研究对象,科学评价其2016—2020年水质和富营养化时空变化特征及关键驱动因素,探讨其成因及治理对策. 结果表明,“十三五”时期长江中游湖泊水质和富营养化程度存在较大差异,与2016年相比,2020年大通湖水质改善最为明显,梁子湖水质变差,总磷是影响长江中游湖泊水质类别的主要因子; 洪湖富营养程度恶化最为严重,斧头湖次之,TLI(SD)对长江中游湖泊富营养化评价贡献最大. 目前长江中游湖泊呈有机污染加重和叶绿素a浓度升高现象,洪湖、斧头湖和梁子湖主要与氮、磷营养盐浓度升高有关,而大通湖、洞庭湖和鄱阳湖受水文过程、流域纳污量和湖泊管理等非营养盐因素影响较大. 总氮和总磷仍然是影响“十三五”时期长江中游湖泊水质和富营养化的最主要驱动力,且各湖泊总氮和总磷浓度变化均具有较强正相关性,建议开展河湖氮、磷标准衔接工作,提出河湖氮、磷标准限值或考核目标,以完善河湖水环境质量标准和生态健康影响评价技术规范. 同时,建议长江中游湖泊在开展截污控源、内源控制和生态修复的同时,进一步深化流域管理,特别是对洞庭湖、鄱阳湖、梁子湖和斧头湖等跨行政区湖泊,以提高湖泊治理与修复的系统性和整体性.  相似文献   

14.
三十年来长江中下游湖泊富营养化状况变迁及其影响因素   总被引:9,自引:5,他引:4  
为弄清长江中下游通江/历史通江湖泊富营养化现状、成因及修复策略,对该区域27个大型湖泊和水库开展了4个季度的水质调查,并结合部分湖泊1988-1992年及2008年两个时段富营养化调查成果,分析近30年来长江中下游地区大型湖泊富营养化关键指标变化的特征及其驱动因素.结果表明,目前该区域绝大多数湖泊处于富营养水平,较1980s有明显加重,浮游植物叶绿素a及总磷是最主要的营养状态指数贡献因子;湖泊的富营养化状况与湖泊的江湖连通状况、换水周期等流动性状况、渔业养殖及管理、流域纳污、治理强度等人类活动方式和强度密切相关;与历史调查结果相比,氮、磷的增幅相对较小,而有机质污染程度明显加重、浮游植物叶绿素a浓度大幅增高,表明营养盐之外的其他因素,如水文节律的变化、江湖阻隔、不合理的渔业养殖活动等,对该区域湖泊的富营养化问题加剧、浮游植物生产力增高起到更为重要的作用.因此,从治理途径和策略上来看,增加湖泊的流通性、恢复部分湖泊的自然水文波动节律、优化湖泊渔业管理、提升湖泊流域营养盐的有效截留能力、实施湖泊生态修复工程是控制长江中下游湖泊富营养化、提升区域湖泊生态质量的关键.  相似文献   

15.
This paper is a review of research works concerning the nutrient transportation, transformation and exchange between water, sediment and biota in the lakes from the middle and lower reaches of the Yangtze River conducted in the context of project entitled "The Processes and Mechanism of Lake Eutrophication in Middle and Lower Reaches of Yangtze River". All the lakes from this area are shallow lakes. According to the typical lake site research, the lakes from the middle and lower reaches of Yangtze River have a higher baseline of nutrition in the history. Normally the trophic status of these lakes can be categorized into medium-trophic or eutrophic. Human activities have been enhanced during the last decades, which speed up the lake eutrophic process. Lake eutrophication control needs to reduce not only the external nutrient inputs from watershed but also the internal loading from the sediments. Investigations revealed that the lake sediments in this area are considerablly high in nutrition in which at most about 30% of phosphorus exists in the form of bio-available in the sediment. The surface sediment will exert great effects on the nutrient exchange between water-sediment interface via adsorption and release of nutrient. The nutrient release from the sediment in these shallow lakes is mainly in two ways, i.e. in the undisturbed condition the nutrient is released through diffusion created by the nutrient gradient from sediment to overlying water; whereas in disturbed condition, the nutrient release is determined by the hydrodynamic forcing intensity and the sediment resuspension. Metallic elements such as the iron, manganese and aluminium and the aerobic-anaerobic ambience will affect the release of nutrients. The disturbed release will increase the total nutrients in the water column significantly in the short period. At the beginning of sediment resuspension, the dissolved nutrient concentration will increase. This increase will be damped if the ferric oxide and aluminium are rich in sediment because of the adsorption and flocculation. This means that the lakes have capability of eliminating the nutrient loadings. Investigations for the lakes from middle and down stream of Yangtze River have suggested that most lakes have the self-cleaning capability. Dredging the control of the internal loading, therefore, is only applicable to the small lakes or undisturbed bays which normally are situated nearby the city or town and rich in organic materials in the sediment. In addition, the strong reduction condition and weak aeration of these lakes and bays make these small lakes and bays release much more bio-available nutrient and without much self-eliminating capability. Moreover, eutrophication induced algal bloom in these lakes will change the pH of water, which further induces the increase in the nutrient release. In turn, the increase in nutrient release promotes the growth of phytoplankton and results in severe algal bloom. For the heavily polluted water, research suggests that the biomass of bacteria and alkaline phosphatase activity will be higher corresponding to the higher concentration of nutrients, which accelerates the nutrient recycling between water, sediment and biota. Quick recycling of nutrient, in turn, promotes the production and biomass growth of microorganism and leads to more severe eutrophication. Further research work should focus on the nutrient transformation mechanism and the effects of microbial loop on the eutrophication.  相似文献   

16.

This paper is a review of research works concerning the nutrient transportation, transformation and exchange between water, sediment and biota in the lakes from the middle and lower reaches of the Yangtze River conducted in the context of project entitled “The Processes and Mechanism of Lake Eutrophication in Middle and Lower Reaches of Yangtze River”. All the lakes from this area are shallow lakes. According to the typical lake site research, the lakes from the middle and lower reaches of Yangtze River have a higher baseline of nutrition in the history. Normally the trophic status of these lakes can be categorized into medium-trophic or eutrophic Human activities have been enhanced during the last decades, which speed up the lake eutrophic process. Lake eutrophication control needs to reduce not only the external nutrient inputs from watershed but also the internal loading from the sediments. Investigations revealed that the lake sediments in this area are considerablly high in nutrition in which at most about 30% of phosphorus exists in the form of bio-available in the sediment. The surface sediment will exert great effects on the nutrient exchange between water-sediment interface via adsorption and release of nutrient. The nutrient release from the sediment in these shallow lakes is mainly in two ways, i.e. in the undisturbed condition the nutrient is released through diffusion created by the nutrient gradient from sediment to overlying water; whereas in disturbed condition, the nutrient release is determined by the hydrodynamic forcing intensity and the sediment resuspension. Metallic elements such as the iron, manganese and aluminium and the aerobic-anaerobic ambience will affect the release of nutrients. The disturbed release will increase the total nutrients in the water column significantly in the short period. At the beginning of sediment resuspension, the dissolved nutrient concentration will increase. This increase will be damped if the ferric oxide and aluminium are rich in sediment because of the adsorption and flocculation. This means that the lakes have capability of eliminating the nutrient loadings. Investigations for the lakes from middle and down stream of Yangtze River have suggested that most lakes have the self-cleaning capability. Dredging the control of the internal loading, therefore, is only applicable to the small lakes or undisturbed bays which normally are situated nearby the city or town and rich in organic materials in the sediment. In addition, the strong reduction condition and weak aeration of these lakes and bays make these small lakes and bays release much more bio-available nutrient and without much self-eliminating capability. Moreover, eutrophication induced algal bloom in these lakes will change the pH of water, which further induces the increase in the nutrient release. In turn, the increase in nutrient release promotes the growth of phytoplankton and results in severe algal bloom. For the heavily polluted water, research suggests that the biomass of bacteria and alkaline phosphatase activity will be higher corresponding to the higher concentration of nutrients, which accelerates the nutrient recycling between water, sediment and biota. Quick recycling of nutrient, in turn, promotes the production and biomass growth of microorganism and leads to more severe eutrophication. Further research work should focus on the nutrient transformation mechanism and the effects of microbial loop on the eutrophication.

  相似文献   

17.
The concentrations and distribution of polychlorinated biphenyls were determined in water, surface sediments and fishes from the estuaries of Pearl River, PR China. The results showed that the concentrations ranged from 2.47 ng l-1 to 6.75 ng l-1 in water, from 11.13 ng g-1 to 23.23 ng g-1 in sediments (dry weight) and from 68.64 ng g-1 to 316.85 ng-1 in fish (lipid weight). It was found that the feeding habits of fish were very significant in the accumulation of polychlorinated biphenyls and pattern of congeners. Carnivorous and benthic fishes such as eel (Anguilla japonica) and Chinese sea catfish (Arius sinensis) were found to have high concentrations of polychlorinated biphenyls and of high-chlorinated congeners, while herbivores such as shad (Clupanodon punctatus) and mullet (Mugil cephalus) exhibited an opposite trend. Congeners IUPAC Nos. 153, 138, 118, 87/81, 170 and 52 were found frequently in most samples (both sediment and fish). In comparison with other places in the world, the concentration of polychlorinated biphenyls in sediment and fish from the estuary of Pearl River were low.  相似文献   

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