长江中下游典型浅水湖泊表层水体微塑料时空分布特征——以湖北保安湖为例

以湖北保安湖为研究对象,分别于2021年4、7、10月和2022年1月采集表层水样,测定水体中微塑料丰度、粒径、形状、颜色和类型,探究浅水型湖泊表层水体中微塑料的时空分布特征及其影响因素。结果表明,保安湖表层水体微塑料的年平均丰度为(16.20±2.23)items/L。微塑料丰度呈现明显的季节性差异,其中夏季(采样时间7月)平均丰度最低,为(1.40±0.09)items/L。在所有微塑料颗粒中,粒径0.064～1 mm占比最大,为82.57%;黑色和无色微塑料占主导地位,占比分别为36.16%和21.31%;纤维状微塑料分布最广泛,占比达40.01%;聚乙烯(PE)和低密度聚乙烯(LDPE)是最主要的微塑料类型,两者之和占比达46.05%,其次为聚苯乙烯(PS,占比17.2%)、聚对苯二甲酸乙二醇酯(PET,占比8.33%)和聚乙酸乙酯(PVAC,占比8.31%)。统计分析表明,微塑料丰度与湖水水质无显著相关关系。该研究揭示了长江中下游地区典型浅水湖泊微塑料分布现状,为评估类似湖泊微塑料潜在污染风险提供了科学依据。     

应用物种敏感性分布评价中国湖泊水体中重金属污染的生态风险

为总体了解我国主要湖泊水体重金属污染现状与生态风险,本文通过历史数据收集,利用物种敏感性分布(SSD)模型与主成分分析法,分析了我国18个湖泊或水域中6种重金属(Zn、Cd、Cr、Cu、Hg和Pb)的分布情况以及其对湖泊淡水生物的潜在生态风险(PAF)和联合生态风险(ms PAF).结果表明:在18湖泊中,6种重金属在湖泊水体中的浓度由高至低依次为Zn(均值为17.06μg/L,范围为4.03~29.33μg/L)、Pb(均值为9.33μg/L,范围为0.04~33.7μg/L)、Cr(均值为5.56μg/L,范围为0.65~40.0μg/L)、Cu(均值为3.71μg/L,范围为0.02~10.2μg/L)、Cd(均值为1.17μg/L,范围为0.01~13.6μg/L)和Hg(均值为0.19μg/L,范围为0.03~1.04μg/L);18个湖泊中重金属的分布情况由3个主成分反映,F1(Cu、Zn、Hg)、F2(Pb、Cd)和F3(Cr、Cu)的贡献率分别为28.50%、24.17%和18.40%,其分布情况受经济和地域差异影响较小;SSD模型显示,不同重金属对全部淡水生物的HC5值不同,从小到大依次为CuCrHgCdPbZn,淡水生物对重金属Cu的敏感性最高,对重金属Zn的敏感性最低;将选取的18个湖泊按ms PAF排序,由高到低依次为呼伦湖(67.0%)鲁湖(56.7%)洱海(52.7%)金银湖(52.3%)太湖(40.5%)墨水湖(39.3%)滆湖(30.2%)鄱阳湖(26.8%)洪泽湖(23.1%)高宝卲伯湖(22.4%)巢湖(20.7%)乌梁素海(19.7%)东湖(19.1%)梁子湖(4.0%)汤逊湖(2.0%)洞庭湖(1%)洪湖(0)=骆马湖(0).研究结果对于了解我国淡水湖泊水质现状和环境安全风险具有重要意义,为湖泊的进一步保护与管理提供了一定的科学依据.     

大通湖及东洞庭湖区生物体重金属的水平及其生态评价

于2005年11月采集了大通湖及东洞庭湖区湖水和水生生物样品,并测定了水和水生生物样品中重金属(Cd、Pb、Hg、As)的含量,并对湖区生物体重金属进行了污染评价.研究结果表明,大通湖及东洞庭湖区湖水中重金属含量较小,绝大部分采样点水质都属于国家Ⅰ类水标准;水生生物体内CD、Pb含量为虾＞螺＞鱼,Hg的含量为鱼＞螺＞虾,As的含量为螺＞虾＞鱼;而鱼类重金属含量则为底栖鱼类＞中上层鱼类,肉食性鱼类＞植食性鱼类.大通湖及东洞庭湖区生物体中CD、Pb的污染指数为虾＞螺＞鱼,Hg的污染指数则为鱼＞螺＞虾,As的污染指数则为螺＞虾＞鱼.     

太湖流域滆湖底泥重金属赋存特征及其生物有效性

为了探讨太湖流域滆湖底泥重金属(Cd、Cr、Cu、Zn、Ni和Pb)的赋存特征及其生物有效性,对底泥重金属总量、形态以及生物富集量进行了分析.结果表明,6种重金属含量的空间分布表现为北部湖区最高,其次为南部湖区,中部湖区最低,重金属Ni、Cu、Zn和Pb含量显著高于沉积物背景值,分别是背景值的4.77、3.89、2.96和2.76倍,重金属总量与沉积物中的黏土成分含量具有显著相关性.采用三级四部提取法对重金属形态进行分析表明,6种重金属的生物有效态(弱酸结合态、可还原态和可氧化态之和)含量顺序为CdCuZnPbNiCr,其中Cd、Cu、Zn和Pb的生物有效态含量分别占总量的84.15%、78.47%、76.50%和64.29%.Cu和Zn在铜锈环棱螺中富集含量要显著高于其他金属元素.相关性分析表明,6种重金属中仅Cr和Pb的生物富集量与有效态含量具有显著相关性,这表明,重金属在生物体内的富集不仅与有效态含量有关,还与底泥重金属总量有关.因此,评价滆湖重金属的生态风险时需要综合考虑重金属的总量及生物有效态含量.     

鄱阳湖饶河段重金属污染水平与迁移特性

鄱阳湖饶河入湖段是鄱阳湖重金属污染最严重的水域之一,为了研究其污染现状,本文于2005年3月平水期对鄱阳湖饶河段的水体、底泥、土壤及水生植物的重金属污染水平及迁移特性进行了调查与分析．结果表明,饶河段水体中的重金属除Pb的含量超出地表水环境质量标准Ⅲ类标准外,其它各项监测指标均能达到地表水环境质量Ⅲ类标准．饶河段底泥及河滩土壤的重金属含量平均值与国家土壤环境质量相比,Zn、Cd的平均值超出了三级标准,而Cu、Pb的含量指标均符合三级标准;通过地质积累指数评价结果表明,饶河段重金属底泥除Zn污染为中度污染以外,其他各种重金属污染为轻度污染或偏中度污染,且饶河段底泥中Cu、Zn、Ph三种重金属元素之间呈极显著正相关．饶河段水生植物对Cu、 Zn、Ph都有不同程度的富集;根据富集系数评价表明,植物对Cu的平均富集能力相对较强些,其次是Pb和Zn,多数水生植物表现出对Cd具有一定的抗性．     

40年来江苏石梁河水库重金属污染的沉积记录

根据石梁河水库沉积物粒度和重金属元素(Cu,Cr,Zn,As和Pb)含量的分析,结合137Cs放射性比活度精确定年,研究了石梁河水库沉积速率和重金属的污染变化特征,并利用地累积指数法评价了重金属的污染程度.结果表明:石梁河水库 40年来平均淤积速率为3.85cm/a,Cu,Cr和zn地累积指数一直小于1,处于轻微污染;As污染水平变化较大.现处于低水平的轻度污染;Pb污染水平自柱底始持续恶化,目前地累积指数大于1,且有污染加剧趋势.     

鄱阳湖“五河”入湖口沉积物中微塑料污染物的特征及其时空分布

微塑料作为新型环境污染物正日益受到人们密切关注,为探索微塑料在鄱阳湖流域的污染状况,以鄱阳湖流域"五河"入湖口的沉积物为研究对象,分别在3个水文周期（平水期、丰水期和枯水期）选择6个典型区域采集沉积物进行分析.采用浮选分离方法及金相显微鉴定技术,分析鄱阳湖"五河"入湖口沉积物中微塑料的类型、丰度和表面形貌等特征,旨在揭示鄱阳湖沉积物中微塑料的空间分布规律及不同水位期的动态变化.研究结果显示微塑料的类型有碎片类、发泡类、薄膜类和纤维类,其中主要以碎片类微塑料为主,所占百分比为51.95%;70%的微塑料粒径<1 mm,微塑料（<5 mm）的平均丰度为811.11 n/kg,6个样点的微塑料丰度值表现为朱港 > 吴城 > 渡头乡 > 龙口 > 瑞洪镇 > 南矶山.6个样点的微塑料丰度值与鄱阳湖水位动态均具一致性,在枯水期所占比例最高,达到44.41%;平水期次之,达到31.52%;丰水期所占比例最低,仅占24.07%.不同水期、不同样地存在不同程度的微塑料污染问题警示人们要重视塑料垃圾的排放及其污染问题,以减少对湖泊、河流等湿地生态环境的影响.     

太湖流域滆湖围网拆除后沉积物营养盐和重金属空间分布特征及评价

为评估滆湖围网拆除工程实施效果,采用高密度网格化布点方法,系统分析滆湖沉积物营养盐和重金属的空间分布和污染特征;并基于有机氮评价方法、综合污染指数评价方法、重金属地质累积指数法和重金属潜在生态风险评价方法进行污染风险评价.结果表明,滆湖沉积物总氮(TN)、总磷(TP)和总有机碳(TOC)的平均含量分别为(3709±1004)mg/kg、(1127±650) mg/kg和(78.39±23.88) mg/g,三者空间分布特征较为一致;营养盐综合污染指数评价表明,全湖整体为重度污染,其中全湖TN均处于重度污染状态,TP绝大部分区域也处于重度污染状态.沉积物重金属Zn、Cr、As、Pb、Ni、Cu、Cd 的平均含量分别为(170.62±47.25)、(105.18±34.91)、(68.55±10.86)、(52.43±14.73)、(44.04±11.93)、(42.57±12.43)、(1.55±1.06) mg/kg,整体上呈现出由南向北、自西向东逐渐增加的趋势,重金属含量最高值在湖区东北角;地积累指数法和潜在生态风险指数法评价结果均表明Cd和As是主要的生态风险贡献因子,其中Cr和Ni的污染程度表现为清洁,Cr、Ni、Cu、Zn和Pb的单项潜在生态风险等级表现为轻微风险.与围网拆除前比,湖中区西南部沉积物营养盐含量无显著变化,湖南区南部沉积物营养盐状况明显改善,但其余各区域沉积物营养盐状况均有不同程度的恶化;湖区沉积物中重金属元素平均含量均有极大程度的降低,降幅在29.50%～80.45%之间,表明在外源污染输入得到一定控制时,围网拆除在控氮、控磷效果及改善重金属污染状况方面有着积极作用.     

基于筛分水平浓度法的洞庭湖沉积物质量基准初步分析

基于2013 2015年调查获取的129个洞庭湖表层沉积物和底栖生物的调查数据,应用筛分水平浓度法初步探讨了洞庭湖沉积物几种重金属沉积物质量基准的推荐值.结果表明,洞庭湖沉积物砷(As)、镉(Cd)、铬(Cr)、铜(Cu)、铅(Pb)和锌(Zn)含量均值为17.2、2.63、56.9、32.4、38.4和96.3 mg/kg(DW);筛分水平浓度法获取的洞庭湖沉积物As、Cd、Cr、Cu、Pb和Zn质量基准分别为11.97、1.13、42.03、19.17、23.63和67.54 mg/kg(DW).通过与不同国家及地区指定的重金属质量基准推荐值以及本地区采用其他方法推导的重金属基准推荐值进行比较,推算出本研究获取的6种重金属沉积物质量基准推荐值接近所有数据的中间值.对于洞庭湖流域,不同方法获取的沉积物重金属质量基准具有可比性.然而,鉴于用于推导沉积物质量基准的数据采集涉及的区域较为有限,且除了重金属污染外,影响底栖生物分布的因素较为复杂,导致获取的沉积物重金属质量基准推荐值存在一定的不确定性.     

武汉典型湖泊沉积物中重金属累积特征及其环境风险

采集武汉市8个典型湖泊的表层沉积物,分析11种重金属的含量及其不同形态组成,研究了不同湖泊金属元素的富集与污染程度,探讨了沉积物中重金属的污染来源及其潜在生态风险,结果表明,沉积物中重金属Cd累积最严重,Zn和Hg也发生明显累积,龙阳湖污染较重,南太子湖和墨水湖污染中等,其它湖泊污染总体较轻.沉积物性质对重金属累积的影响不显著,城市工业活动强烈影响着重金属的分布,不同重金属的形态分布差异较大,Cd生物可利用态含量最高,其次为Mn、Zn、Co、Cu和Pb;而Sb和Hg以残留态占绝对优势,生态风险较小,相关分析和主成分分析表明,化石燃料燃烧、金属冶炼等是武汉市湖泊沉积物中重金属来源的主要贡献者,同时岩石风化等地球化学过程也影响着重金属的污染.     

洞庭湖流域湘江铜锈环棱螺(Bellamya aeruginosa)的重金属富集特征及其膳食风险评估

洞庭湖流域对湘江湖南段6个城市江段铜锈环棱螺（Bellamya aeruginosa）腹足和内脏团的As、Cd、Pb、Cu、Zn、Cr富集量进行分析,运用单因子污染指数法评价其受污染程度,并分别采用平均每周/每月摄入量法和目标危害系数法对其膳食风险进行评估,旨在为湘江流域居民铜锈环棱螺的消费安全提供参考.结果显示,铜锈环棱螺腹足As、Cd、Pb、Cu和Zn的富集量均值分别为0.92、1.65、0.90、13.01和67.62 mg/kg,Cr未检出,As、Cd、Pb和Cu的超标率分别为87.06%、27.06%、24.72%和2.35%.内脏团As、Cd、Pb、Cu、Zn和Cr的富集量均值分别为9.61、3.21、3.75、33.58、169.05和1.23 mg/kg,As、Cd、Pb、Cu和Cr超标率分别为100%、71.76%、65.88%、14.12%和75.8%.所有江段成人As、Cu和Zn的每周摄入量均值和最高值均低于FAO/WHO食品添加剂联合专家委员会（JECFA）提出的暂定每周耐受摄入量参考值（PTWI）,但株洲成人Cd的每月摄入量均值超过其每月耐受摄入量参考值,且最大值是其参考值的3.44倍,永州、湘潭地区成人Cd的每月摄入量最大值也分别是其参考值的1.16和1.68倍.所有江段铜锈环棱螺摄入的单一重金属健康风险值除As外均小于1,但多种重金属复合暴露健康风险值均接近或大于1.结果表明,湘江湖南段6个城市江段铜锈环棱螺均受到一定程度的污染,其中衡阳、湘潭和株洲江段较为严重,且各江段铜锈环棱螺内脏团重金属富集量整体上均高于腹足,故当地居民长期食用后存在潜在的健康风险.     

Phytoremediation of heavy metal‐contaminated water and sediment by Eleocharis acicularis

Phytoremediation is an environmental remediation technique that takes advantage of plant physiology and metabolism. The unique property of heavy metal hyperaccumulation by the macrophyte Eleocharis acicularis is of great significance in the phytoremediation of water and sediments contaminated by heavy metals at mine sites. In this study, a field cultivation experiment was performed to examine the applicability of E. acicularis to the remediation of water contaminated by heavy metals. The highest concentrations of heavy metals in the shoots of E. acicularis were 20 200 mg Cu/kg, 14 200 mg Zn/kg, 1740 mg As/kg, 894 mg Pb/kg, and 239 mg Cd/kg. The concentrations of Cu, Zn, As, Cd, and Pb in the shoots correlate with their concentrations in the soil in a log‐linear fashion. The bioconcentration factor for these elements decreases log‐linearly with increasing concentration in the soil. The results indicate the ability of E. acicularis to hyperaccumulate Cu, Zn, As, and Cd under natural conditions, making it a good candidate species for the phytoremediation of water contaminated by heavy metals.     

乌梁素海大气重金属沉降入湖通量初步估算

重金属元素以大气颗粒物为载体,最终以沉降的方式进入湖泊水体,会引起湖泊的重金属污染.为调查大气沉降对乌梁素海重金属污染的贡献,于2013年7月1日至30日围绕乌梁素海进行大气沉降样品采集,分别测定Cu、Zn、Pb、Cd、Cr、Hg、As 7种重金属元素的含量,并在此基础上估算7月大气重金属沉降通量及入湖量.结果表明,乌梁素海重金属元素大气沉降通量大小依次为:ZnPbCuCrAsHgCd.结合社会调查情况及数据分析显示,大气微粒携带重金属借助风力迁移,较大的沉降通量出现在主风向的下风向区域,说明风向是影响乌梁素海大气重金属沉降通量的主要因素之一.排干输入与大气沉降方式下的乌梁素海重金属入湖量比较发现,大气沉降是除排干输入外湖泊的另一重要重金属污染源.Zn、Pb、Cu、Cr、As、Hg、Cd等重金属元素月入湖量分别为10.6、1.04、1.02、0.833、0.342、0.00514、0.00281t/月.通过估算底泥重金属增量来评价大气沉降对湖泊重金属的贡献表明,大气Hg、Zn、Pb、Cu、As、Cd、Cr等重金属沉降对湖泊贡献率分别为46.4%、44.7%、14.1%、12.0%、8.48%、4.75%、4.03%.     

Distribution and Chemical Forms of Heavy Metals in the Flood 1997 Sediments of the Upper and Middle Odra River and its Tributarie:, Poland

At the beginning of August 1997, 72 samples of flood sediments were taken along the Upper and Middle Odra river and its tributaries. The concentrations of Zn, Pb, Cu, Cd, Co, Ni, Cr, Mn, and Fe in the bulk samples and in the <20 μm fraction were determined by AAS method. The contents of metals vary in wide ranges and are significantly higher in the <20 μm fraction of sediments. The range concentrations vary as following: Zn 274...3 656 mg/kg, Pb 79...1 773 mg/kg, Cd 1.7...11.8 mg/kg, Cu 38...2 244 mg/kg, Cr 14...384 mg/kg, Co 4...73 mg/kg, Hg 0.2...3.9 mg/kg, Mn 214...6 972 mg/kg, and Fe 1.5...16.3 %. The highest amount of the metals was found in the Wrocław and Głogów regions. The mobile (exchangeable and carbonatic fractions) portions of metals reached up to 50 % of Zn, 40 % of Pb and Cu and 60 % of Mn.     

Assessment of heavy metal contamination in the sur?cial sediments from the lower Meghna River estuary,Noakhali coast,Bangladesh

Sediment samples were collected from ten selected sites of the lower Meghna River estuary, and six heavy metals were analyzed with Atomic Absorption Spectrophotometry(AAS) to assess the contamination level and the metals' association with sediment grain size. The current results revealed that the mean concentrations of the studied metals were ranked in descending order of iron(Fe)(1.29 ? 103 mg/kg) zinc(Zn)(42.41 mg/kg) lead(Pb)(12.48 mg/kg) chromium(Cr)(10.59 mg/kg) copper(Cu)(6.22 mg/kg) cadmium(Cd)(0.28 mg/kg). The geo-accumulation, contamination, and pollution load indexes suggested that the lower Meghna river estuary was not contaminated by Fe, Zn, Pb, Cr, and Cu.The mean size of the sediment ranged from 28.92 to 126.2 mm, and the Pearson correlation coefficient showed a significant association between Fe and Pb(coefficient of determination, r2? 0.836; p 0.05),and no significant correlation was found between individual metals and grain size, indicating no or low influence on the metals distribution.     

Sediment pollution and its effect on fish through food chain in the Yangtze River

Suspended sediment adsorbs pollutants from flowing water in rivers and deposits onto the bed. However, the pollutants accumulated in the river bed sediment may affect the bio-community through food chain for a long period of time. To study the problem the concentration of heavy metals （Cr, Cd, Hg, Cu, Fe, Zn, Pb and As） in water, sediment, and fish/invertebrate were investigated in the middle and lower reaches of the Yangtze River during 2006-2007. The concentrations of heavy metals were 100-10,000 times higher in the sediment than in the water. Benthic invertebrates had relatively high concentrations of heavy metals in their tissues due to their proximity to contaminated sediments. Benthic invertivore fish had moderately high concentrations of heavy metals whereas phytoplanktivore fish, such as the silver carp, accumulated the lowest concentration of heavy metals. The concentrations of Cu, Zn, and Fe were higher than Hg, Pb, Cd, Cr, and As in the tissue samples. The concentration of heavy metals was lower in the river sediments than in the lake sediments. Conversely, the concentration of heavy metals was higher in river water than in lake water. While a pollution event into a water body is often transitory, the effects of the pollutants may be long-lived due to their tendency to be absorbed in the sediments and then released into the food chain. The heavy metals were concentrated in the following order： bottom material 〉 demersal fish and benthic fauna 〉 middle-lower layer fish 〉 upper-middle layer fish 〉 water.     

Content and distribution of trace metals in surface sediments from the northern Bering Sea, Chukchi Sea and adjacent Arctic areas

Concentrations of trace metals (Zn, Cr, Cu, V, Cd and Pb), total organic carbon (TOC), black carbon (BC) and their granulometry were examined in 25 surface sediment samples from the northern Bering Sea, Chukchi Sea and adjacent areas. Trace metal concentrations in the sediments varied from 21.06-168.21 mg kg(-1) for Zn, 8.91-46.94 mg kg(-1) for Cr, 2.69-49.39 mg kg(-1) for Cu, 32.46-185.54 mg kg(-1) for V, 0.09-0.92 mg kg(-1) for Cd, and 0.95-15.25 mg kg(-1) for Pb. The geoaccumulation index (Igeo) indicated that trace metal contamination (Zn and Cd) existed in some stations of the study area. The distribution of grain size plays an important role in influencing the distribution of trace metals (Zn, Cr, Cu, V, and Pb) in sediments from the Chukchi Sea and adjacent areas.     

Concentration of 7 Heavy Metals in Sediments and Mangrove Root Samples from Mai Po, Hong Kong

Concentration of 7 heavy metals, Zn, Fe, Cu, Cr, Cd, Pb and Ni in mudflat sediments, mangrove root sediments and root tissues of Acanthus ilicifolius, Aegicerus corniculatum and Kandelia candel from the Mai Po Nature Reserve, Northwest Hong Kong, were measured. Metal concentrations in the upper 0–10 cm of the sediment cores from the mudflat were 4–25% higher than those found in the bottom 21–30 cm. Relative Topsoil Enrichment Index approximated 1.0 for all the metals. Mudflat sediment concentrations of Fe, Ni, Cr, Cd and Cu were greater than those found in the mangrove sediments. Except for Fe, concentrations of the other 6 heavy metals were more elevated in the mangrove root sediments than in the corresponding root samples. Higher concentration factors for Zn, Fe and Cu may indicate bioaccumulation. Mean metal concentrations in both mudflat and mangrove sediments decreased in the order Fe > Zn > Pb > Ni > Cu > Cr > Cd. Mangrove root tissues also showed the same pattern except that Pb > Cu > Ni     

太湖浮游植物中重金属含量的季节变化特征及湖区差异

近年来随着社会经济的发展,排入太湖的污水中重金属含量不断增加,为研究太湖浮游植物中重金属的污染状况,分别于2009年春季(4月)、夏季(7月)和冬季(12月)对太湖不同湖区展开调查,通过HCA聚类分析和Pearson相关分析探讨不同湖区浮游植物中重金属含量的季节变化,并与优势藻种进行CCA分析,对浮游植物重金属与各藻种关系进行初步探讨.结果表明:太湖浮游植物中重金属的含量大小为:ZnMnPbCuNiCrAsCdHg,其中Zn、Cu、Mn、Pb、Ni的季节变化明显,Zn和Cu、Pb、Ni、Cr之间的相关系数很高且具有同源性.通过对比不同湖区,发现北部梅梁湾的浮游植物重金属含量较高,东太湖和湖心区含量均低于沿岸湖区.CCA分析表明春季重金属与优势藻种呈正相关,而夏季和冬季二者呈负相关.三季中重金属与蓝藻和绿藻的相关性最高,与隐藻的相关性最低.蓝藻中,重金属与铜绿微囊藻的相关性高于水华微囊藻.