中国红树林湿地有机污染物研究进展

随着经济的发展, 分布于热带、亚热带沿海潮间带的红树林遭受到各类污染物的威胁。各种陆源有机污染物严重威胁着红树林湿地的水体、沉积物及生物体。汇总我国红树林生态系统水、沉积物及生物体内多环芳烃、多氯联苯、有机氯农药、抗生素、溴代阻燃剂等机污染物的研究结果, 进而评价我国红树林生态系统的有机污染现状及生态风险。总体来看, 已有多种污染物在红树林水体、沉积物及生物体中检出, 有机污染物含量处于较低水平。红树林水体中有农药及抗生素检出; 沉积物中多环芳烃、多氯联苯含量在珠江口地区最高, 二者在沉积物中的潜在生态风险较低; DDT 在红树林沉积物中的生态风险属于较低水平, 但部分红树林区DDT 含量存在超过ERM 的现象, 应引起重视;多溴联苯醚等“新型”有机污染物在珠江口红树林沉积物中普遍检出。多种有机污染物在红树林植物及林内生物体种存在生物富集效应。红树林是多种有机污染物的重要蓄积地。     

黄河三角洲石油化工区农田土壤-玉米体系PAHs的分布特征及风险评价

为明确黄河三角洲石油开采区表层土壤和玉米中多环芳烃（PAHs）的含量及其污染水平,采集农田土壤和玉米各71个样品,检测农田土壤和玉米各部位中16种PAHs含量,并采用内梅罗指数法和健康风险评价模型评估了农田土壤中多环芳烃的生态健康风险。结果表明,农田土壤、玉米根、茎和叶中多环芳烃的含量分别为256.6-1936、291.4-680.9、324.9-527.9、289.5-2400 μg/kg。农田土壤中多环芳烃以4-6环为主。多环芳烃在玉米根茎叶富集系数大小排序为：叶 > 茎 > 根。玉米不同组织中PAHs浓度与相应农田土壤中PAHs浓度的进行相关分析结果表明,农田土壤中PAHs含量与玉米根、茎中PAHs含量均存在极显著正相关关系,相关系数分别为0.98（P<0.01）、0.98（P<0.01）,表明玉米根和茎的多环芳烃主要来源于农田土壤中,农田土壤中PAHs的含量影响着PAHs在玉米根茎中的积累和分布。玉米叶中PAHs含量与农田土壤中PAHs含量与玉米根、茎中PAHs含量不存在相关关系,表明玉米叶中多环芳烃并非来自土壤中PAHs的迁移,可能来源于大气。内梅罗指数结果表明,农田土壤PAHs达到了中度污染,其中BaA、Pyr和BbF达到了偏重污染;健康风险评价结果表明,农田土壤PAHs对儿童和成人的平均非致癌风险分别为0.44和0.12（均小于1）,表明农田土壤多环芳烃对成人和儿童的非致癌风险是可接受;农田土壤PAHs对儿童和成人的平均致癌风险分别为3.6×10^-5、9.0×10^-6,没有超过致癌风险水平上限（10^-4）,致癌风险尚在可接受范围内。3种暴露途径中,皮肤接触是土壤PAHs的最主要暴露方式,其次是经口摄食,吸入暴露途径甚微,可忽略不计。PAHs对儿童健康的威胁风险要大于成人,所以应尽可能避免儿童直接接触或误食土壤等其他介质的污染物。     

水体沉积物中微生物厌氧呼吸耦合多环芳烃降解的研究进展

多环芳烃(Polycyclic aromatic hydrocarbons,PAHs)是一种具有致癌、致畸、致突变的持久性有机污染物。本文在分析国内外主要水体沉积物中PAHs污染状况的基础上,综述了近几年有关厌氧水体沉积物中微生物以硝酸盐、Fe(III)以及硫酸盐为电子受体进行呼吸耦合PAHs降解的研究概况。此外,还总结了基于微生物的PAHs降解基因组、蛋白质组、代谢组以及菌群水平上互作网络的研究进展,以期为进一步加速PAHs污染水体沉积物原位生物修复提供科学理论参考。     

中国城市污泥土地利用关注的典型有机污染物

污泥土地利用是国内外城市污泥主要的处置方式之一,而污泥中的有机污染物是污泥土地利用的限制性因素之一.本文分析了国内外城市污泥中有机污染物的浓度和研究现状,针对我国国情,认为多环芳烃(PAHs)是城市污泥中一种常见的有机污染物,总含量一般在1 ～ 10 mg·kg-1,有的因污水来源复杂而超过了100 mg·kg-1;壬基苯酚(NP/NPE)在我国污水处理厂污泥样品中均有检出,浓度在1～128 mg·kg-1.污泥园林绿化、林地利用、土壤改良等将是今后主要的利用方向,要实现污泥安全、环保的土地利用,多环芳烃(PAHs)和壬基苯酚(NP/NPE)将是主要考虑的典型有机污染物.     

长江口南支表层沉积物中多环芳烃分布特征及生态风险

2008年5月和8月先后2次采集长江口南支表层沉积物样品,采用高效液相色谱进行多环芳烃测定,研究其分布、来源与生态风险。结果表明:长江口南支表层沉积物中PAHs总量在8.9~312.2ng.g-1;PAHs组成以芘、菲、苯并[b]荧蒽、苯并[a]蒽、苯并[a]芘为主,各站芘的含量均最高,本研究PAHs总含量与长江口、黄河口和鸭绿江口近期的调查数据相近,但明显低于珠江口和闽江口数据,以及长江口潮滩沉积物中PAHs数据;PAHs环数组成以中、高环为主,表明长江口南支PAHs主要来源于相对高温条件下不完全燃烧过程。采用平均效应中值商法评价长江口南支PAHs生态风险结果表明,调查区域PAHs产生生态风险的概率较小(<10%)。     

河网地区小城镇街尘的粒径分布与多环芳烃污染

街尘是重要的环境介质,其携带的污染物在城镇化过程中对河网地区的水环境构成了一定的威胁。以杭嘉湖平原河网地区饮用水水源河流上游典型小城镇的街尘为研究对象,对街尘、河道沉积物、地表径流以及降雨前后地表水中的多环芳烃进行测定。在对不同粒径街尘中多环芳烃浓度的测定中发现,粒径为<63、125-63、250-125和900-250 μm街尘中多环芳烃的平均含量分别为7261、5835、4660和2909μg/kg。小粒径的街尘颗粒含有较高的多环芳烃浓度,较小的密度,并且较难清扫,造成了小粒径街尘易被雨水冲刷随地表径流进入河网水体。在对两场降雨的地表径流中多环芳烃检测发现,颗粒态的多环芳烃分别占总浓度的95%和94%。地表径流过程增加了受纳水体中多环芳烃浓度的43%-62%,其中超过50%的增加表现为颗粒态。在对不同河段沉积物、地表径流中颗粒物和不同粒径街尘中多环芳烃浓度的风险评价中发现,小粒径街尘和地表径流中颗粒物中多环芳烃的浓度相接近并具有较高的生态风险,城镇段河道沉积物较次之。由于河网地区的特殊的水文条件和景观空间格局特征,地表径流沉积物在进入河网水体后易原位沉积,造成了河道沉积物城镇段有较高的多环芳烃浓度。     

不同介质中多环芳烃光降解及与生物耦合降解研究现状

多环芳烃(PAHs)是环境中广泛存在的一类有机污染物。它的降解一直是人们关注的课题。光降解就是多环芳烃降解的一种重要形式。对在气相、液相和固相不同介质中的PAHs光降解研究进行了综合论述,重点对PAHs在液相介质的降解速率及影响因素、中间产物及降解机制和反应动力学进行了深入探讨,并介绍了光-生物耦合降解多环芳烃的研究进展。建立系统而有效的PAHs光降解研究技术与方法,是目前当务之急。进一步完善PAHs光降解研究的技术与方法,可更准确地研究PAHs光降解机制及影响因素。     

多环芳烃污染生物修复研究进展

多环芳烃(polycyclic aromatic hydrocarbon,PAHs)是一类对环境有严重危害的持久性有机污染物。具有高生物富集性、致癌性、致毒性和难降解性,修复治理PAHs污染环境备受国内外政府及学者的关注。目前主要采用物理、化学以及生物方法对多环芳烃污染的土壤和水体进行修复。其中生物修复是一种高效、经济和生态可承受的环保技术,具有成本低、无二次污染等优点。本文从植物修复、微生物修复以及植物-微生物联合修复方面,阐述了国内外生物修复PAHs污染的最新研究进展。指出了生物修复PAHs污染环境需要进一步解决的问题,并对未来发展趋势进行了展望。     

白洋淀表层沉积物多环芳烃风险的空间分布

利用气相色谱-质谱法(GC-MS)测定了白洋淀表层沉积物16种优控多环芳烃的含量,应用统计分析、分子异构体比值、空间插值等方法分析其组成特征、空间分布,进行了风险评价。结果表明,白洋淀表层沉积物中16种优控多环芳烃总量在1.79～1618.90 ng·g^-1,均值为411.12 ng·g^-1。多环芳烃组成以4环和5环为主,分别占总含量的42.22%和28.21%,单体含量最高的是苯并[b]荧蒽,占比为16.47%,最低的为苊,占比仅为0.26%。说明白洋淀多环芳烃来源于本地输入,较少受到气团输送的影响。多环芳烃空间分布为淀区中心浓度高,四周浓度低,污染尤以淀中心西北部和南部为重,包括安新大桥、烧车淀、采蒲台,其次是寨南和端村。源解析显示,白洋淀表层沉积物多环芳烃含量受木材秸秆等生物质燃烧、煤炭燃烧和石油燃烧的综合影响。生态风险评价结果显示,约1/3的采样点位超过效应区间低值,存在潜在的生态危害。比较2007、2008、2009、2016年的检测数据发现,多环芳烃的平均含量有所下降,可能与淀中村人口密度下降和煤改电有关。     

城市土壤中多环芳烃分布和风险评价研究进展

随着城市化进程的加快,城市土壤中的多环芳烃（PAHs）污染日趋严重.本文从城市土壤中多环芳烃的分布和来源等方面综述了国内外取得的最新研究成果,对影响城市土壤多环芳烃分布的人为因素、自然因素,常见的多环芳烃源解析方法,以及城市土壤多环芳烃污染的风险评价进行了全面的阐述,尤其对地统计学在多环芳烃空间分析及风险评价上的应用进行了总结.最后,对未来城市土壤中多环芳烃研究的重点与发展趋势进行了展望.     

Mobility of iron in the estuaries of the Rhine and the Ems relevant to plant-availability problems

Studies were undertaken to obtain information on the iron mobilization processes in the sediments of the rivers Rhine and Ems, both located in western Europe. On their way from the fresh-water tidal area to the marine environment these sediments loose a considerable amount of their iron. The iron is released from the sediment by means of biodegradation products of the organic matter which dissolve the iron as organic iron complexes. The major functional groups of these organic compounds responsible for the iron mobilization are carboxyls and phenolic hydroxyls. From the sediments of the river Ems greater amounts of organic iron compounds are dissolved than from sediments of the river Rhine. Also fewer organic compounds are released from marine sediments than from fresh-water sediments, which indicates a diminished iron mobility in the marine area of the delta. Besides this the organic compounds from the marine sediments show an impoverishment in their functional groups. The sediments of the rivers Rhine and Ems are also distinguished by a different occupation of functional groups in the organic compounds. On account of a number of experiments the mobilization capacity of these river systems have been discussed.From a viewpoint of plant nutrition the mobility of iron in deposits of different ripening stages was also investigated.     

Vertical Profile of PAHs and Dredging Depth of River Sediments

Sediment dredging is an effective engineering measure to reduce the negative effects of PAHs pollution on water environment. The dredging depth is a key parameter in environmental dredging engineering. A guidance of environmental dredging depth needed to reduce the toxicity risk was developed which was specifically designed for the removal of river sediments contaminated by PAHs based on the mean effect range median quotients (mean-ERM-q). The dredging depths for removing river sediments were calculated based on the vertical profile of PAHs content and the quality guidelines of sediment. Pinghu water system was carried out to determine the dredging depths of sediments from nine rivers by the proposed method. Each sediment core was collected from different river. The results showed the profiles of PAHs in sediment cores were irregular and diverse due to river dredging events and human activities in different periods. The risk assessment of PAHs toxicity showed one of nine cores with moderate-high probability, 4 of nine cores with low-moderate probability and the others with low toxicity risk. The achievement can offer a reference to the dredging engineering in other similar river systems.     

Polycyclic Aromatic Hydrocarbons in Sediments: An Overview of Risk-Related Issues

This series of articles address site-specific issues associated with evaluating exposure and toxicity of polycyclic aromatic hydrocarbons (PAHs) in sediments. These include factors that influence the opportunity to come into contact with PAHs in sediments (bioaccessibility) and those that affect the potential for transfer from sediment to ecological and human receptors (bioavailability). Although organic carbon is viewed as an important matrix for sorbing PAHs, studies have shown that there are various forms of carbon, some of which are highly sorptive. These latter forms vary on a site-specific basis and including this form of carbon in the assessment can reduce the uncertainty associated with estimating exposure. Other site-specific factors associated with water clarity, depth, and light penetration can result in enhanced toxicity of PAHs as a result of photoactivation. Chemical analyses of sediments increasingly include the alkylated PAH compounds. Although analyses of this suite of PAH compounds is being conducted to support ecological assessments and forensic analyses, there is little guidance on how to interpret the alkylated PAHs with respect to human health risks. An approach for accomplishing this is suggested.     

Application of P450RGS reporter gene system as a bioindicator of sediment PAH contamination in the vicinity of Incheon Harbor, Korea

Sixty seven sediment samples were collected from Kyeonggi Bay, Korea, including the mouth of Han River, Incheon Harbor, the Namdong industrial complex, and the open sea. Collections were conducted in December, 1995 and samples were maintained frozen (-20 °C) until analysis. Dichloromethane extracts were analysed for their content of CYP1A1-inducing compounds with a P450RGS (reporter gene system) assay, and for polycyclic aromatic hydrocarbons (PAHs). Sediment samples were also analysed for organic carbon (OC) content and grain size, to aid in evaluating the relationship between contamination and physical nature of the sediments. The responses of the P450RGS assay to the sediment extracts were expressed as μg of benzo[a]pyrene toxic equivalents per g dry weight (μg g^-1 BaPTEQ), and these values correlated well (r² = 0.624 with total PAHs. BaPTEQ values were also highly correlated with the OC content of the sediments. The determination of P450RGS BaPTEQ is a useful tool, because it is both a rapid and inexpensive means of assessing the potential toxicity of organic compounds in environmental sediment samples. These values represent an estimate of the levels of compounds in the sediment that are potentially available to organisms through chronic exposure to pore water or ingestion of benthic species. We believe BaPTEQ values are more useful than tables of specific PAH concentrations, if the purpose of the investigation is to either obtain a rapid screening of an area or to develop some form of ecological or human health risk assessment.     

Polycyclic aromatic hydrocarbons in surficial sediments and caged mussels of the St. Marys River, 1985

During 1985, a biological monitoring study was conducted in the St. Marys River to determine the availability and source areas of polycyclic aromatic hydrocarbons (PAHs) and the relative importance of water and sediment to tissue contaminant concentrations. Clean unionid mussels (Elliptio complanata) were exposed in cages for three weeks at 14 stations and surficial sediments were obtained at 12 of these. The highest concentrations of total PAHs as well as many individual compounds were found in sediments and mussels from the Algoma Steel Slip above St. Marys Falls and in sediments below the discharge of the Edison Sault Electric Co. Canal. Although concentrations were lower below the Falls, elevated levels persisted downstream along the Ontario shore into Lake George. PAHs were also accumulated by mussels exposed along the Michigan shoreline, but at lower levels than along the Ontario shore. From 23 to 63 percent of the PAHs in sediments and 6 to 27 percent of those in mussels were comprised of compounds with mutagenic and/or carcinogenic properties. The predominance of higher molecular weight PAHs in both sediments and mussels as well as lower molecular weight PAHs and nitrogen- and sulfur-containing PAHs in certain areas, indicates that high temperature combustion of fossil fuels is the major source of PAHs, augmented by localized spills of fossil fuels and coke oven by-products.Mussels contained fewer PAHs (up to 18 vs. 25) at lower concentrations (µg kg^-1 vs. mg kg^-1) than the associated surficial sediments. Also, mussels suspended at mid-depth in the water column accumulated similar concentrations to those exposed to sediments, indicating that the major exposure pathway is via the water filtered by these organisms, and hence, is due primarily to external industrial inputs.     

Predicting Sediment Toxicity at Former Manufactured Gas Plants Using Equilibrium Partitioning Benchmarks for PAH Mixtures

This study was conducted to examine the application of Equilibrium Partitioning Sediment Benchmarks (ESBs) for assessing the toxicity of polycyclic aromatic hydrocarbons (PAHs) in sediments at former manufactured gas plant (MGP) and coke sites. Samples of freshwater sediment from four MGP and coke sites in the U.S. Northeast and Midwest were analyzed for 34 individual PAHs, total organic carbon, “black” carbon (potentially composed of pitch, soot, and other forms of pyrogenic carbon), and sediment toxicity (28-day Hyalella azteca toxicity test). The sum of the Toxic Units in each sample was calculated from a one-phase model that accounts for sorption of PAHs to total sediment organic carbon, and a two-phase model that accounts for sorption to black carbon as well as to natural organic carbon. Although both the one-phase and two-phase models accurately predicted concentrations of PAHs that were not toxic to aquatic invertebrates, the two-phase model was more often in agreement with results of sediment toxicity tests. While the bioavailability and toxicity of PAHs may vary at other sites, the two-phase model correctly predicted that sediments from these sites with concentrations of total PAHs as high as 52 mg/kg were not toxic to invertebrates.     

Behaviour of selected PCBs,PAHs and γ-HCH in the Scheldt estuary,S.W. Netherlands

The behaviour of some organic micropollutants in the abiotic compartments water, particulate matter and bottom sediments of the Scheldt estuary, S.W. Netherlands, was studied between 1986 and 1989. Special attention was given to two individual PolyChlorinated Biphenyl congeners (PCB 52 and PCB 153), two Polycyclic Aromatic Hydrocarbons (PAHs) fluoranthene and benzo(a)pyrene and γ-HCH. Dissolved PCBs and γ-HCH behave conservatively during estuarine mixing. The concentration of γ-HCH in the fresh-water is extremely high in spring compared to the other seasons. Dissolved fluoranthene does not behave conservatively. The concentration of dissolved fluoranthene in the freshwater endmember shows a seasonal dependence with highest concentrations in winter and lowest in summer. Benzo(a)pyrene could hardly be detected in the dissolved phase with the methods used. PCBs and PAHs in particulate matter and sediments behave essentially conservatively as a result of the mixing of riverine particulates with high, and marine particulates with low organic micropollutant contents. Particulate fluoranthene is removed at low salinities under (nearly) anoxic conditions probably by microbial degradation. The rivers Scheldt and Rupel appear to be the major sources for the compounds studied. However, in particular the organic micropollutant contents of the sediments indicate that important emissions along the estuary were or are still present. Measurements of individual PCBs and PAHs in the <63 μm fraction of a dated sediment core from a salt marsh in the eastern part of the Scheldt estuary show that the recent input of PCBs and PAHs into the estuaryis probably 2–3 times lower than the maximum input in the mid-1960s. The PCB profile shows postdepositional congener-selective mobilization caused by advective transport. The PAH assemblage is remarkably uniform in the sediment core. The PAH ratios indicate that combustion of coal is the main source of PAHs in the Scheldt estuary.     

In situ treatment of Hamilton Harbour sediment

To enhance the biodegradation of organic contaminants, approximately 18.5 tonnes of oxidant (calcium nitrate) and 5 tonnes of nutrients were injected into sediments of the Dofasco Boatslip, Hamilton Harbour. In the laboratory 78% and 68% of the oil (TPHs) and polynuclear aromatic hydrocarbons (PAHs), respectively biodegraded in 197 days. In the 1992 treatment in the Ddofasco Boatslip, biodegradation of organic contaminants varied from 79% for low molecular weight compounds (BTXs), to 25/15 of the 16 priority pollutant PAHs. At first biodegraduation of large molecular weight PAHs resulted in the production of naphthalene (from 280 g/g to 549 g/g). In the 1993 treatments, 94% of the naphthalene, and 57% of the TPHs biodegraded. The in situ biotreatment of organic contamination takes time but for some sites the significantly lower cost relative to dredging and confinement makes in situ treatment a viable alternative.     

Culture-independent study of bacterial communities in tropical river sediment

Ubiquitous microbial communities in river sediments actively govern organic matter decomposition, nutrient recycling, and remediation of toxic compounds. In this study, prokaryotic diversity in two major rivers in central Thailand, the Chao Phraya (CP) and the Tha Chin (TC) distributary was investigated. Significant differences in sediment physicochemical properties, particularly silt content, were noted between the two rivers. Tagged 16S rRNA sequencing on a 454 platform showed that the sediment microbiomes were dominated by Gammaproteobacteria and sulfur/sulfate reducing Deltaproteobacteria, represented by orders Desulfobacteriales and Desulfluromonadales together with organic degraders Betaproteobacteria (orders Burkholderiales and Rhodocyclales) together with the co-existence of Bacteroidetes predominated by Sphingobacteriales. Enrichment of specific bacterial orders was found in the clayey CP and silt-rich TC sediments, including various genera with known metabolic capability on decomposition of organic matter and xenobiotic compounds. The data represent one of the pioneered works revealing heterogeneity of bacteria in river sediments in the tropics.