珠江(广州河段)表层沉积物中重金属的分布特征及相关性研究

随着广州市截污工程的实施,珠江(广州河段)外源污染得到有效控制后,沉积物内源污染将成为影响河流水质的重要因素。在珠江(广州河段)表层沉积物中8种重金属质量分数监测的基础上,对该河段沉积物中重金属的沿程分布特征和横向分布特征进行了全面的分析,并对所测8种重金属之间的相关性进行了研究。结果表明:从沿程分布来看,这8种污染元素的分布特征基本相似,元素的高值区和低值区大致吻合。从横向分布来看,绝大多数污染物在一个断面的最高值和最低值出现的点位基本上是重合的,各种污染物质量分数的最高值绝大部分出现在靠近岸边的点位,并且大部分集中于左岸。而最低值出现在河道中间的比例较高。在所测定的8种元素中,除了Hg和As之外,其它各种元素之间均呈现较明显的正相关关系,特别是Cr和Cd、Cu和Cd、Cr和Cu、Cr和Ni之间的相关性显著。     

珠江广州段水体微塑料的时空分布特征及生态风险评估

珠江河流微塑料入海通量在世界河流中处于中上水平,流经广州市区的珠江各支流带来的陆基微塑料是珠江入海微塑料的主要来源,其微塑料污染特征和潜在生态风险值得进一步研究。分别在秋季和冬季在珠江广州段的19个监测点的微塑料污染现状开展了调查,采用Manta拖网过滤法采集水体表面0-0.5 m深的微塑料样品。结果显示,珠江广州段河流水体微塑料丰度在秋季和冬季分别为0.092-26.4 pieces·m^-3和0.044-2.07 pieces·m^-3,在全国乃至全世界范围内处于中等水平。处于广州市中心区的采样点微塑料丰度远高于入海口,水体微塑料丰度的最高点(26.4 pieces·m-3)出现在位于市内区域的采样点,该点位于广州市老城区,主要以生活区为主,人口密集,证实了人为活动对水体微塑料分布的影响。聚酰胺/尼龙、聚丙烯和聚乙烯这三类聚合物是检出的主要聚合物类型,占据所有微塑料样品的80%以上。在所有微塑料中,透明色和白色居多,其他颜色未发现明显的规律特征,粒径小于2 mm的小尺寸微塑料丰度占比高于大尺寸微塑料,碎片类和纤维类的微塑料在所有样品中均频繁检...     

阜阳城区水体浮游动物群落周年结构特征及其与水质的关系

于2011年3月到2012年2月逐月对阜阳城区几条主要河流：颍河（A）、泉河（B）、西城河（C）、东城河（D）、南城河（E）、西清河（F）、中清河（G）、东清河（H）及三角洲（I）水体进行设点采样,研究各水体浮游动物的结构特征及多样性水平,并分析了各水体浮游动物的生物量与相应水体主要水质指标的相关关系。结果表明：浮游动物密度在各水体一年中出现两个高峰,分别在4—5月和10月,生物量也有两个高峰,分别比相应密度高峰晚一个月左右;这些高峰与水质指标具有相伴关系;各水体浮游动物生物量与相应水体主要水质指标（CODCr,、BOD、DO、TP、NH。-N）具有显著的相关关系。因此,阜阳城区各水体浮游动物生物量与水体污染程度有一定关系,可根据浮游动物生物量来判别相应水体水质,但鉴于水生态环境的复杂性,在监测水质时,其它生物因子也应综合考虑。     

平原河网地区农村生活污染入河机制

以太滆运河流域前黄镇和雪堰镇为研究区,设计农村生活非点源污染调查问卷,采用随机抽样的方法,调查了39个行政村中85个自然村的农村生活污染情况。通过对问卷的统计分析得到了厕所使用类型的比例、化粪池中上清液和固体残渣的去向以及生活垃圾处置等信息。在对农村生活污染进行分类的基础上,估算出该地区农村生活污染入河系数为:CODCr,6.6%～13.3%;TN,18.1%～18.6%;TP,8.2%～12.5%。     

The Distribution and Impacts of Dioxins and Polychlorinated Biphenyls in the Taiwan Er-Jen River

The distribution and impacts of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/DFs) and polychlorinated biphenyls (PCBs) in the Taiwan Er-Jen River were investigated by monitoring fish distribution and measuring PCDD/DFs and PCBs levels in sediment and fish samples. Most of the fish collected are pollution-resistant species such as Oreochromis spp, Liza macrolepsis, Channa spp and Megalops cyprinoides. the most polluted river sections are in the upstream where large amount of waste effluents from households, livestock rearing and nearby dumping sites were discharged into the river, and the lower reaches of the river where metal recovery activities including open burning of waste electrical wire/scrap occurred. Sediment samples collected near the burning site show 2,3,7,8-TCDD toxicity equivalents (TEQ) ranging from 0.014 to 14.2 ng g^-1 by PCDD/DFs and from 0.015 to 1.03 ng g^-1 by coplanar PCBs (Co-PCBs). the fish samples show TEQ ranging from 0.029 to 0.615 ng g^-1 by PCDD/DFs and from 0.012 to 0.12 ng g^-1 by Co-PCBs. Possible PCDD/DFs sources are discharged PCBs, open burning of waste wire/scrap, and pentachlorophenol. the consumption of these fish will cause an average intake of 54 pg kg^-1 d^-1 TEQ. the prevention of direct discharge of livestock and the dumping of waste effuents into River Er-Jen as well as the control of metal recovery activities appears to be the first step toward the restoration of River Er-Jen.     

Assessment of the Water Quality of the River Arno in the Area of Florence,Italy

The quality of the waters collected from R. Arno was examined in the period September 1988 to December 1989. A first campaign in September/October 1988, during a period of low water, gives a general picture of pollution conditions along the river from the source to the mouth. the river appears to be heavily polluted immediately downstream of Florence and in the area of the textile industry.

In the second campaign, through the whole year 1989, particular attention has been given to the Florence area; the most significant results, compared with those from a previous investigation carried out in 1971, show only a small reduction of the pollution load, due to the shortage and inadequacy of wastewater depuration. Some considerations are reported on pollution drop with full spate.     

Assessment of the Water Quality of the River Arno in the Area of Florence, Italy

The quality of the waters collected from R. Arno was examined in the period September 1988 to December 1989. A first campaign in September/October 1988, during a period of low water, gives a general picture of pollution conditions along the river from the source to the mouth. the river appears to be heavily polluted immediately downstream of Florence and in the area of the textile industry.

In the second campaign, through the whole year 1989, particular attention has been given to the Florence area; the most significant results, compared with those from a previous investigation carried out in 1971, show only a small reduction of the pollution load, due to the shortage and inadequacy of wastewater depuration. Some considerations are reported on pollution drop with full spate.     

吉林省松花江中下游污染物排放总量控制

分析了实施总量控制的理论依据 ;并以此研究吉林省松花江中下游污染物总量控制以及吉林市控制单元的总量控制方案 ;最后探讨了总量控制措施。     

邯郸市沁河水污染治理方案

本文对邯郸市沁河水污染现状进行了调查分析,总结了城市内河治理经验,通过方案比较,推荐“清淤,护坡,建坝,分质截污,邯钢废水混凝沉淀处理”为沁河治理方案。     

东北漫岗区村落的分布特征分析

对黑龙江省绥化市的6个村落、九三垦区鹤山农场的8个村落和嫩江县双山镇的蔡窑村进行实地考察。依据鹤山农场1980-1995年气温、日照时数、风速、降水量和≥5级风日数的气象资料,同时考虑到地形、土壤等因素,分析了东北漫岗区村落分布的特征,即：日照和太阳辐射影响了村落分布的坡向,就不同坡向而言,村落分布数量大小顺序为：东南坡、西南坡、东北坡、西北坡;风影响室温,并可能对房屋造成破坏,故大部分村落分布在坡中部以下;降水量和土壤特性决定了村落的分布下限;地理环境因素和人的选择性、能动性共同决定了东北漫岗区村落呈狭长形沿坡分布。     

长江中下游部分城市岸段沉积物中重金属的生物可利用性特征分布

2007年10月对长江中下游部分城市岸段河道底质和边滩共31个站位沉积物中酸可挥发性硫化物(AVS)和4种同时可提取态重金属(SEM)含量及其空间分布特征进行了研究,结果表明:河道底质中∑SEM浓度范围为0.20～0.94μmol/g,平均值为0.45μmol/g;AVS浓度范围为0.01～0.08μmol/g,平均值为0.03μmol/g。边滩沉积物中∑SEM浓度范围为0.35～1.57μmol/g,平均值为0.91μmol/g;AVS浓度范围为0.01～0.14μmol/g,平均值为0.04μmol/g。沉积物中∑SEM与有机碳(R=0.714,p≈0.000)、含水率(R=0.401,p=0.025)和Eh(R=0.368,p=0.042)呈显著正相关关系,而AVS与各个环境因子并不存在显著相关性;依据不同的生物有效性评价方法对沉积物中重金属的生物有效性的判断表明,长江中下游中泓底质沉积物比边滩沉积物中重金属对底栖生物具有更高的潜在危害性。