太湖五里湖区表层沉积物中酸挥发性硫化物和同步提取金属

湖泊底泥中的酸溶硫化物易与二价金属生成难溶金属硫化物,从而制约沉积物中二价有毒金属的化学活性以及生物有效性,进而影响沉积物的环境质量.对沉积物中的酸溶硫化物(AVS)和同步提取金属(SEM)进行测定,依据SEM/AVS的比值可以判定重金属生物有效性.通过对太湖五里湖、梅梁湾表层沉积物夏季和秋季AVS与SEM的采样分析,结果表明:研究区域内AVS的含量夏季高于秋季,SEM受季节影响很小,SEM/AVS大于1,且秋季高于夏季,初步判断该湖区沉积物中重金属具有潜在的生物毒性.     

抚仙湖表层沉积物AVS与SEM分布特征及其生态风险评估

以高原深水抚仙湖为研究对象,分析了全湖16个样点表层沉积物（0~5 cm）的酸可挥发性硫化物（AVS）和同步提取重金属（SEM）的分布特征,并利用∑SEM和AVS的物质的量浓度比对全湖重金属潜在生态风险进行了评估.结果表明：AVS在南北湖区分布存在明显差异,南部湖区分布均匀,平均含量仅为0.074±0.043 μmol/g,而北部湖区则由湖岸带向北湖心（N9）呈现出递增趋势,平均含量高达0.317±0.485 μmol/g.SEM在南北湖区分布较为集中,南部湖区主要集中在路居河口（S2）,北部湖区主要分布在老凹地（N5）和东大河口（N4）.除牛摩河口（S5）、梁王河口（N3）和北湖心（N9）外,其余所有点位[∑SEM]/[AVS]>1,且南部湖区平均[∑SEM]/[AVS]值（3.51±1.91）显著高于北湖湖区（2.19±2.10）.因此抚仙湖全湖尤其是南部湖区重金属生态风险应引起高度重视.     

富硫型水库沉积物AVS和SEM空间分布特征及重金属风险评价

随着湖库外源性污染的有效控制,沉积物污染特征成为影响湖库水环境质量的关键因素。本文以富硫型水库——汤河水库为研究对象,分析探讨水库沉积物的理化性质、重金属总量、酸可挥发性硫化物(acid volatile sulfide,AVS)和同步提取重金属(simultaneously extracted metals,SEM)的空间分布特征,采用沉积物基准法(sediment quality guidelines, SQGs)和AVS与SEM关系法对重金属可能诱发的生态风险和毒性效应进行评估。结果表明:汤河水库沉积物中AVS含量在0.03~51.75 μmol/g之间,并呈现坝前深水区>东支流库区>西支流库区的空间分布特征。根据Pearson相关性分析可知,汤河水库沉积物AVS含量与间隙水中SO₄^2-浓度、沉积物烧失量(LOI)含量呈显著正相关,与沉积物间隙水中NO₃^-浓度和沉积物pH呈现显著负相关。间隙水中SO₄^2-浓度和沉积物LOI含量是控制AVS产量的重要因素。水库沉积物中ΣSEM变化范围为0.52~2.75 μmol/g,呈现出东支流库区>坝前深水区>西支流库区的分布规律。水库沉积物中ΣSEM/AVS和ΣSEM-AVS的变化范围分别为0.06~22.73和-49.18~2.44 μmol/g,显示出水库坝前深水区表层0~10 cm沉积物不具有生态风险,而东、西支流库区沉积物中的SEM因为不能完全被AVS所固定而存在潜在生态风险。就单一重金属而言,汤河水库坝前深水区和东西支流中部区域沉积物Ni、Cu、Pb和Zn含量均介于临界效应含量(threshold effects level, TEL)值和可能效应含量(probable effect level, PEL)值之间,可产生低级风险毒性效应,但Ni的毒性效应风险接近中级,今后应予以重点关注。富硫型水库沉积物中容易出现高含量AVS,沉积物间隙水中SO₄^2-和NO₃^-的浓度是决定沉积物AVS净产量的重要因素。流域内重金属土壤背景值以及工业、采矿产业排放的废水类型直接影响着诱发生态风险的重金属种类。     

武汉东湖沉积物中重金属生物有效性研究

沉积物中的酸挥发性硫化物(AVS)是预测厌氧沉积物中重金属生物有效性的重要参数,SEM/AVS大于1时沉积物中重金属具有潜在生物毒性,小于1时则无生物有效性. 本文研究了东湖三个不同污染负荷的站点的同步提取金属SEM(Cu, Zn, Pb, Cd, Ni, Co, Ag, Cr)和SEM/AVS的深度分布,研究表明东湖沉积物中主要重金属是Zn, Cr和Cu,约占SEM总量的90%. I站、II站沉积物中AVS是重金属生物有效性的主控因子之一,对重金属的深度分布影响较大,重金属不具有生物有效性;III站沉积物中AVS对重金属的深度分布影响较小,重金属具有潜在的生物毒性. 相关分析表明,I站、II站沉积物中Cr、Ni、Ag、Cd与AVS在P<0.05有显著性相关,AVS对这些金属的深度分布具有更强的控制作用;虽然两站沉积物中Cr的含量差别不大,东湖I站沉积物中Cr/AVS比值(0.02)显著高于II站(0.003),沉积物中Cr与硫化物的结合主要是受还原反应的影响.     

武汉东湖沉积物中酸挥发性硫化物(AVS)的深度分布及其影响因素

提要沉积物中酸挥发性硫化物(AVS)是硫化物的生成、氧化和扩散等综合作用的反映,有机物的供给、硫酸盐的还原等因素都能影响其分布特征。本文对武汉东湖三个污染程度不同站点的AVS深度分布特征进行了研究,结果表明,AVS含量在一定深度沉积物中具有最大值,东湖沉积物中AVS的深度分布具有两种不同的模式,Ⅰ站和Ⅱ站AVS浓度峰在5cm左右的表层沉积物中,且AVS还原层深度较狭窄,而Ⅲ站AVS浓度峰处于10-20cm深度范围,沉积物中有机质负荷的差异是导致这种分布特征的重要原因。沉积物中有机质含量对AVS的深度分布具有重要影响,高有机质负荷导致AVS浓度峰向表层迁移,且AVS还原层分布于较狭窄的深度范围,对方涛等对流-扩散模型的应用表明,该模型在高有机质负荷沉积物中(Ⅰ、Ⅱ站)AVS深度分布的应用较为理想,然而低有机质负荷沉积物中(Ⅲ站)不能准确反映AVS的深度分布特征,说明其应用范围具有一定的局限性。     

长江中下游湖泊沉积物中磷的形态及藻类可利用量

调研了长江中下游地区25个浅水湖泊的35个样点表层沉积物中磷的地球化学形态特征,以及太湖沉积物中藻类可利用磷(AAP)的空间分布,垂向分布特征及其蓄积量,探讨了浅水湖泊表层沉积物中磷的赋存量,地球化学形态及其与水草,湖水磷浓度,叶绿素(Chl-a)浓度之间的关系.结果表明,长江中下游地区浅水湖泊的表层沉积物中可交换态磷(Ex-P)含量与水体总磷(TP),溶解性总磷(DTP)及溶解性反应活性磷(SRP)浓度关系密切,有水草湖区的沉积物中生物易利用磷(Bio-P)含量显著低于无水草湖区及藻型湖区.太湖梅梁湾沉积物泥芯中,表层3 cm沉积物中Ex-P含量显著增高,而夏季还原条件下容易转变为溶解态磷的铁磷(Fe-P)含量峰值则出现在4～10cm深度.太湖表层沉积物的Bio-P含量与夏季叶绿素浓度密切相关,说明表层沉积物的Bio-P及AAP可以作为沉积物内源释放风险的指示参数.太湖表层1 cm底泥中所含有的AAP量估计多达268.6吨,风浪扰动能将大量的AAP带入水体,对太湖蓝藻水华暴发起着不可忽视的作用.     

太湖表层沉积物中有机氯农药残留及遗传毒性初步研究

采用GC-ECD对太湖表层沉积物中的有机氯农药含量进行了定性定量分析.太湖20个采样点均有不同程度的有机氯农药检出,16种有机氯农药总量为4.22-460.99ng/g(dw),北部湖区、潮心区以及沿岸区等均有高值点出现,与沉积物有机质含量、氮磷营养盐含量分布并不一致.检出率最高的有机氯农药组分为DDTs、HCHs.DDTs含量检出顺序为P,P'-DDT>P,P'-DDD>P,P'-DDE,说明环境中可能仍然具有DDT箱入特征;HCHs中?HCH,?HCH检出相当,怃-HCH检出较高,主要为早期残留.结合鼠伤寒沙门氏菌/哺乳动物微粒体酶系(Ames)试验研究太湖典型溯区表层沉积物中有机污染物的遗传毒性,初步确定可能的生态风险因子.     

白洋淀沉积物重金属潜在生态风险及生物可利用性分析

沉积物是湖泊水体重金属的主要汇集场所,也是湖泊重金属污染研究及整治的重点.本文分析了白洋淀多个淀区沉积物中16种重金属含量水平及垂向分布特征,解析了其中典型有害重金属潜在生态风险,并基于酸可挥发性硫（AVS）及同步可提取金属（SEM）、间隙水溶解态金属、可转化态金属形态分级等研究,对重金属生物可利用性进行了分析.结果表明：沉积物重金属含量均值高低依次为Fe （29630.50 mg/kg）>Ti （3213.07 mg/kg）>Mn （539.44 mg/kg）>Zn （104.01 mg/kg）>V （76.63 mg/kg）>Cr （52.60 mg/kg）>Cu （43.49 mg/kg）>Ni （35.83 mg/kg）>Pb （26.75 mg/kg）>Co （10.32 mg/kg）>As （8.96 mg/kg）>Mo （2.06 mg/kg）>Sb （1.57 mg/kg）>Tl （0.43 mg/kg）>Cd （0.31 mg/kg）>Hg （0.16 mg/kg）;其中,10种重金属在各淀区沉积物中呈现出自北往南逐渐降低的趋势,各金属在不同淀区分布差异性主要由污染输入所致.除北部烧车淀区域外,其余区域重金属潜在生态风险总体处于较低水平.重金属污染主要来源于该区域周边河道,但近10年来污染输入及在沉积物中的富集总体趋于稳定并呈逐渐降低的趋势.入淀污染不仅增加了该区域沉积物中重金属总量,也使得其中可转化态重金属比例较高,大多在30%~90%之间,提升了重金属生物可利用潜力.水生植物等内生性有机质的大量富集导致沉积物还原性较强,AVS含量较高,沉积物中AVS和ΣSEM均值分别为（10.59±6.37）和（2.23±1.53）μmol/g （dw）.Cd、Cu、Ni、Pb、Zn等金属由于高含量还原态硫的固定而生物可利用性较低.然而,As和Hg在这样的高有机质和强还原环境下更容易溶解和释放,是潜在生物可利用性相对较高的金属,在间隙水中的浓度分别达到（17.07±0.23）和（2.39±0.94）μg/L,未来研究及整治中应给予更多关注.     

南太湖区域表层沉积物中有机氯化合物及重金属污染现状

对南太湖水域表层沉积物中的19种有机氯化合物及6种重金属的含量、分布及其生态风险进行了研究和评价.所测样品中有机氯农药(OCPs)和多氯联苯(PCBs)含量范围分别为0.51 -4.98、1.49-15.15ng/g(dw),与国内其它水域沉积物中OCPs、PCBs的含量相比处于较低水平.OCPs中的主要污染物是α-六...     

洱海流域入湖河口湿地沉积物氮、磷、有机质分布及污染风险评价

以云南洱海罗时江河口湿地为典型对象,利用柱状底泥分层采样器采集罗时江河口湿地表层(0~10 cm)沉积物样品,研究分析总氮(TN)、总磷(TP)、有机质(OM)的空间分布特征,并对沉积物进行污染风险评价.结果表明:表层沉积物TP含量在0.04~1.28 g/kg之间,空间分布特征为:Ⅱ区Ⅰ区,水道Ⅰ水道Ⅱ;TN含量在0.33~2.96 g/kg之间,空间分布特征为:Ⅰ区Ⅱ区,水道Ⅰ水道Ⅱ,OM含量在32.43~233.03 g/kg之间,空间分布表现为Ⅰ区Ⅱ区,水道Ⅰ水道Ⅱ.结合综合污染指数与有机指数评价法可知,罗时江河口湿地表层沉积物氮、磷污染:Ⅰ区和水道Ⅰ属于中度污染,Ⅱ区和水道Ⅱ属于轻度污染;有机污染:水道Ⅰ和水道Ⅱ属于重度污染,Ⅰ区和Ⅱ区属于中度污染.罗时江河口湿地表层沉积物空间分布受外源污染物、养殖活动和湿地水生植物的影响,氮、磷外源输入以水道Ⅰ为主,有机质输入以水道Ⅱ为主.     

The distribution of acid-volatile sulfide and simultaneously extracted metals in sediments from a mangrove forest and adjacent mudflat in Zhangjiang Estuary, China

The distribution of acid-volatile sulfide (AVS) and simultaneously extracted metals (SEM) were studied in sediments collected from mangrove forest, forest fringe and adjacent mudflat in the Zhangjiang Estuary, China. The aim was to examine the spatial distribution of AVS and SEM in sediments of the Estuary and determine the influence of mangrove trees on AVS and SEM concentrations in the sediments. The results indicated that AVS concentrations in forest sediments were significantly lower than those in mudflat sediments. There was a significant positive correlation between AVS values and moisture contents in forest sediments, while LOI played an important role in AVS concentrations of mudflat sediments. In the forest sediment core, the peak value of AVS appeared deeper in the sediment profile compared to it appeared in the mudflat core. The distribution of SEM showed different trends from that of AVS, and potential toxicity existed in the upriver forest sediments.     

Reactive sulfides relationship with metals in sediments from an eutrophicated estuary in Southeast Brazil

The potential association of acid-volatile sulfides (AVS) and reactive (HCl soluble) Fe with the distribution of reactive trace metals (Cu, Cd, Ni, Pb and Zn) was investigated in sediment cores collected in the Igua?u river estuarine system (Guanabara bay, Brazil), within the river (core R) and the bay (core B) areas. Moderate to extremely high AVS concentrations (33-314 micromol g(-1)) were found in the rapidly-accumulated sediments of this eutrophicated estuary. AVS showed significant correlations with Fe, Ni and Pb in core B, whereas no correlation between AVS and metals was observed in core R. Results suggest that the AVS:Fe molar ratio may often reflect the diagenetic conditions controlling the distribution of Cd and Cu in core B better than AVS and Fe levels themselves. A shift in the biogeochemical controls of metal distribution from the river to the open bay sediments is suggested, with a greater association of most metals with AVS and Fe in bay sediments.     

Assessment of heavy metal impact on sediment quality of the Xiaoqinghe estuary in the coastal Laizhou Bay,Bohai Sea: Inconsistency between two commonly used criteria

Surface sediments in the Xiaoqinghe estuary, southwestern coastal Laizhou Bay, were examined to assess the bio-toxic risk of heavy metals (Cd, Cu, Ni, Pb and Zn) with the effects range-low and effects range-median guidelines (ERL–ERMs) and the concentration ratio of simultaneously extractable metals to acid volatile sulfides ([SEM]/[AVS]). Based on the ERL–ERM guidelines, bio-toxic effect caused by Cu, Ni, Pb and Zn could be expected in the riverine surface sediments of the Xiaoqinghe estuary; and the surface sediments in the marine area were in good quality and only Ni might cause bio-toxic effect occasionally. The AVS–SEM guidelines revealed that no bio-toxic effect could be caused by any of the studied metals in both the riverine and marine sediments, since there were excess sulfides in surface sediments which could form water-insoluble substances with free metal ions and reduce the bioavailability of heavy metals.     

Distribution and sources of organochlorinated contaminants in sediments from Izmir Bay (Eastern Aegean Sea)

Eighteen surface sediment samples representative of the entire Izmir Bay were analyzed for organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs). This was in order to provide extensive information concerning the recent deposition of these compounds in this area, together with levels, distribution, possible sources and potential biological risk. Sites that were contaminated by high concentrations of organochlorine compounds were associated with dense population, such as the harbour and the Gediz River estuary. Relatively higher ΣDDT concentrations and high DDT/DDE + DDD ratios in the Gediz River estuary indicated DDT usage, probably linked to public health emergencies. According to the established guidelines for sediment quality, the risk of adverse biological effects from such levels of OCPs and PCBs as recorded at most of the study sites was insignificant. But the higher concentrations in Inner bay and in the Gediz River estuary could cause biological damage.     

Impact of millennial mining activities on sediments and microfauna of the Tinto River estuary (SW Spain)

In this paper, we analyze two short cores collected in the Tinto estuary (SW Spain), and describe the palaeoenvironmental evolution of this area during the last two millennia, along with the influence of historical mining activities and recent industrial pollution on sediments and microfauna (foraminifera and ostracoda). Although there were no significant changes in the distribution of microorganisms, a first pollution period (0-150 AD) was recorded in high sediment pollution by Cu in the shallow palaeochannels of the middle estuary. During this period and the following 1700 years, tolerant pioneer species of both foraminifera and ostracoda were found predominantly in the inner, protected areas of the estuary, while the bottom sediments were subjected to high hydrodynamic gradients, and consequently showed lower density and diversity of organisms. In the last 150 years, acid mine drainage processes, introduction of a new mining period, and the polluted inputs derived from two industrial processes resulted in increased heavy metal contamination of the bottom sediments, and corresponding extirpation of ostracodes and restriction of foraminifers to the inner zones of the estuary.     

Distribution and Fate of Organochlorine Pollutants in the Pearl River Estuary

Samples of surface sediment and suspended particulate matter (SPM) were collected from the Pearl River estuary, China, and the distribution and concentration of hexachlorocyclohexanes (HCHs), DDTs and polychlorinated biphenyls (PCBs) were extensively studied. The concentration ranges of HCHs, DDTs and PCBs in the sediments were 0.28–1.23 ng g⁻¹, 1.36–8.99 ng g⁻¹ and 0.18–1.82 ng g⁻¹, respectively. The concentrations of HCHs, DDTs and PCBs in the SPM varied both with the sampling locations and the season of collection. Higher concentrations were recorded in the SPM as compared with sediments. The distribution pattern of such organochlorine compounds (OCs), in the Pearl River estuary, showed that sources were some major river mouths and input from Shenzhen Bay. The concentrations of OCs were, however, low as compared with other estuaries and seas. The environmental fate of the OCs during estuarine mixing was determined, in part, by physicochemical and biochemical properties. The absorption and sedimentation of SPM were also considered important factors. Marine sediments may, therefore, be regarded as an important reservoir of hydrophobic and persistent OCs.     

Input and behaviour of linear alkylbenzenesulphonates (LAS) in a stratified estuary

Input and distribution of linear alkylbenzenesulphonates (LAS) in the highly stratified Krka River estuary were studied during 1990–1991. Determinations of individual LAS homologues in wastewater and estuarine waters were performed using reversed-phase high-performance liquid chromatography (HPLC) with spectrofluorimetric detection. The investigated municipal wastewaters contained LAS homologues with alkyl-chain lengths from C₁₀ to C₁₃ at total concentrations in the range of 285–1041 μg l⁻¹. Total LAS input via wastewaters into ibenik Harbour, the most polluted part of the estuary, was estimated at 12.6 kg day⁻¹. A relatively large fraction of total LAS, depending on the wastewater particle load, was found in particulate form (11–59%). Distributions of the individual homologues in dissolved and particulate fractions were rather different, the latter being significantly enriched in higher homologues (C₁₂, C₁₃). The LAS concentration in the estuary was quite low (0.2–23.9 μg l⁻¹) which was caused chiefly by a strong and fast dilution process. However, characteristic vertical distribution of LAS in the estuarine water column indicated that the wastewater plume spreads almost exclusively in the upper (brackish) layer. The concentration maxima were observed in the surface microlayer and at the brackish water/seawater boundary.     

Influence of the Aznalcóllar mining spill on the vertical distribution of heavy metals in sediments from the Guadalquivir estuary (SW Spain)

The Natural Park of Do?ana and the Guadalquivir estuary were impacted by the release of 6 million cubic meters of acid waste after the mine-tailing spill in Aznalcóllar (Andalusia, SW, Spain). Here is presented the monitoring of the accidental spill on vertical distribution of heavy metals in the estuarine sediments. The total concentration of six metals (Fe, Mn, Zn, Cd, Pb, Cu), their chemical speciation and the organic carbon concentration were analyzed in sediment vertical profiles. The results obtained determine background levels similar to previously reported in the area. The analysis catalogues the impact of the accident on the estuary as acute and mainly associated with high concentrations of Zn and Cd. The recent enrichment in Zn and Cd and their geochemical association with the more mobile fractions of the sediment determine an environmental risk associated with the acute impact and detected in some of the areas of the estuary.