ECONOMIC EFFECTS OF RIVER RECREATION ON LOCAL ECONOMIES1

ABSTRACT: Outdoor recreation is a major, growing use of water resources in the United States. The economic effects of expenditures by visitors to three recreational river sites on local economies surrounding the sites were estimated using an input-output model (IMPL.AN). Expenditure data were from the Public Area Recreation Visitors Study (PARVS). Results indicate that visitor spending stimulates a considerable amount of economic activity and growth in local economies. Economic effects include increases in total gross output ranging from $2.6 million to $13.4 million, increases in total income ranging from $1.2 million to $5.6 million, and increases in employment ranging from 60 to 292 jobs.     

毒性鉴别评价方法对城镇污水处理厂去除水中有毒物质的分析实例

以江苏省常州市城北污水算处理厂的进水、活性污泥处理系统的出水以及A^2O处理工艺的出水为研究对象,对进出水进行Daphnia magna急性毒性试验。结果表明,进水对Daphnia magna具有24h急性毒性,经过活性污泥处理工艺处理及A^2O处理工艺处理,两股出水均不显示24h急性毒性,采用毒性鉴别评价（Toxicity Identification Evaluation,TE）方法对进水进行监测和评价,发现曝气可去除进水的毒性,C18固相提取亦可去除进水毒性,进水中存在的主要毒物为易挥发的非极性有机化合物,进一步检测可知,进水中的关键毒物主要为邻丙基甲醛肟、1,1－甲基乙基－2－甲氧基苯酚、2－氮,氮二甲基苯甲醇等,此外,对2个处理系统出水进行GC／MS分析,可知出水中关键毒物基本被去除。     

全氟化合物对水生植物的生态效应研究Ⅱ——金鱼藻对水中PFOS的生物富集及生理响应

为探究全氟化合物对水生植物的生态效应,选择金鱼藻(Ceratophyllum demersum L.)为受试生物,设定5、100、1 000、10 000、50 000、100 000μg·L-1以及对照共7个PFOS浓度梯度进行水培,分析包括超氧化物歧化酶(SOD)、过氧化氢酶(CAT)、过氧化物酶(POD)在内的抗氧化系统酶和细胞色素含量等生理响应特征,并研究金鱼藻对PFOS的生物有效性及富集能力。结果表明:金鱼藻对PFOS的富集量最高可达3 180 mg·kg-1dw,最大富集系数高达40.7倍,可作为PFOS污染水体植物修复的遴选物种。随PFOS浓度升高,SOD活力总体上没有明显变化,但POD活力表现为双重效用,即低浓度促进酶活力积累,而高浓度抑制酶活力积累。CAT活力在低浓度组(0、5、100、1 000μg·L-1),未表现出明显异常,在高浓度组(10 000、50 000、100 000μg·L-1),出现先升高后降低的趋势。色素含量也反应较为敏感,低浓度处理后色素含量升高,高浓度处理则导致色素含量先升高后降低,最高浓度处理下一直处于较低水平,可作为评价PFOS污染水体的生理敏感性指标。     

全氟化合物对水生植物的生态效应研究Ⅰ——典型城市河道全氟化合物的暴露水平及植物富集特征

全氟化合物(perfluorinated compounds,PFCs)近年来得到国内外广泛关注,针对工业源排放区域的环境暴露、来源解析以及动物层面的生态效应有较多研究,但对于普遍存在于非工业源(生活源)的城市河道PFCs暴露及水生植物富集等研究较为缺乏。本研究选择位于北京北部东西贯通的城市河道——清河水体为对象,分析结果表明,清河水体中12种目标PFCs均有检出(总量最高为65.45 ng·L-1),并以全氟丁烷磺酸盐(perfluorobutane sulfonate,PFBS)为主(最高达45.63 ng·L-1);6种水生植物(篦齿眼子菜、黑藻、金鱼藻、芦苇、菖蒲及水葱)的富集物质均以全氟辛烷磺酸盐(perfluorooctane sulfonate,PFOS)和全氟辛酸(perfluorooctanoic acid,PFOA)为主,沉水植物中金鱼藻对于PFOS的蓄积效果优于黑藻及篦齿眼子菜,挺水植物中根部PFCs含量高于茎叶,根部PFOA及PFOS含量高于茎叶,但全氟丁酸(perfluorobutanoic acid,PFBA)含量茎叶则高于根部。整体来看,尽管芦苇、菖蒲和水葱3种挺水植物尚不能作为PFCs的超富集植物,但其根部对PFCs均有显著的吸收效果,具有一定的生态修复潜质;沉水植物中金鱼藻是北方自然河道的优势物种,且对PFOS具有显著的富集效应,因此有必要进一步探索其PFCs生物指示和生态修复功能。     

环境内分泌干扰物低剂量-效应研究进展

环境内分泌干扰物(EDCs)的低剂量-效应已成为生态毒理学界的研究热点.环境内分泌干扰物在接近或低于无可见不良效应浓度水平(NOAEL)时仍可诱发生物效应并存在非单调剂量-效应关系,这对现行的动物繁殖和发育毒理学检测规程以及环境内分泌干扰物风险评价的理论和方法提出了挑战.此外,由于环境中内分泌干扰物呈低剂量长期暴露的特征,研究低剂量-效应对正确进行生态风险评价具有重大的科学意义.在总结国内外相关研究的基础上,对当前环境内分泌干扰物低剂量-效应的研究进展进行了综述.     

Evaluation of the use of bioaccumulation and biological effects tools in caged mussels,within the European Water Framework Directive

Bioaccumulation and biological effects of pollution were assessed in mussels (Mytilus galloprovincialis) caged for one month at three sites in the Oiartzun estuary (south-eastern Bay of Biscay, Spain) with the aim of evaluating their usefulness within the investigative monitoring defined in the European Union Water Framework Directive (WFD). The highest concentrations of organic contaminants determined in mussels' tissue were detected towards the inner part of the estuary but no gradient pattern was found for metal bioaccumulation. Population fitness responses measured as condition index, stress on stress and gonad index were similar in all caged mussels and did not follow the organic pollution gradient. However, biomarkers determined at tissue, cell and protein level (histopathology, micronuclei frequency, malondialdehyde levels and vitellogenin-like protein levels) revealed a higher stress syndrome at the inner part of the estuary showing signs of genotoxicity, oxidative stress and endocrine disruption. Overall, the integrated chemical–biological approach in connection with mussel caging technique proved to be a useful tool to assess environmental pollution, allowing a better understanding of the cause–effect relationship within the investigative monitoring defined in the WFD.     

基于生物导向的水生态健康监测及评估概述

环境监测是水生态健康监测与评估的重要环节,基于物理、化学监测的传统水质监测通常仅能提供独立的数据信息,不能全面、直观地反映水环境状况。基于生物等生命体导向的水生态监测通过生物对环境的响应,能够直接反应复杂水体状况,在水环境健康监测与评估中占据重要地位。基于病原微生物、指示生物介绍了生物监测中的常规生物指标,总结了包括藻类、无脊椎动物和鱼类在内的常见指示生物在不同类型污染水体中的环境指示作用。从生物毒性效应出发介绍了常用的毒性效应测试方法、分析了污染物在不同生物学水平的响应,从而指明生物毒性效应在水环境健康评估中的发展优势。再从生态完整性角度阐述了生态完整性评价的一般方法和新兴分子生物学技术在水生态健康评估中的应用。重点指出环境毒理学和分子生物学在水环境监测的优势,以期为更加科学精确地进行水生态健康监测预警提供支撑。     

Potential Negative Ecological Effects of Corridors

Despite many studies showing that landscape corridors increase dispersal and species richness for disparate taxa, concerns persist that corridors can have unintended negative effects. In particular, some of the same mechanisms that underlie positive effects of corridors on species of conservation interest may also increase the spread and impact of antagonistic species (e.g., predators and pathogens), foster negative effects of edges, increase invasion by exotic species, increase the spread of unwanted disturbances such as fire, or increase population synchrony and thus reduce persistence. We conducted a literature review and meta‐analysis to evaluate the prevalence of each of these negative effects. We found no evidence that corridors increase unwanted disturbance or non‐native species invasion; however, these have not been well‐studied concerns (1 and 6 studies, respectively). Other effects of corridors were more often studied and yielded inconsistent results; mean effect sizes were indistinguishable from zero. The effect of edges on abundances of target species was as likely to be positive as negative. Corridors were as likely to have no effect on antagonists or population synchrony as they were to increase those negative effects. We found 3 deficiencies in the literature. First, despite studies on how corridors affect predators, there are few studies of related consequences for prey population size and persistence. Second, properly designed studies of negative corridor effects are needed in natural corridors at scales larger than those achievable in experimental systems. Third, studies are needed to test more targeted hypotheses about when corridor‐mediated effects on invasive species or disturbance may be negative for species of management concern. Overall, we found no overarching support for concerns that construction and maintenance of habitat corridors may result in unintended negative consequences. Negative edge effects may be mitigated by widening corridors or softening edges between corridors and the matrix. Other negative effects are relatively small and manageable compared with the large positive effects of facilitating dispersal and increasing diversity of native species. Efectos Negativos Potenciales de los Corredores     

道路生态影响评价方法研究：以兰海高速公路为例

提出了将道路生态影响问题划分为3个尺度来进行评价,并根据不同尺度的生态特征采用不同的方法和指标,从而系统、定量的评价道路建设和运行所带来的生态影响.小尺度问题采用野外调查和样方对比的方法;中尺度问题主要依靠不同分辨率的遥感监测,辅之野外调研;大尺度问题主要依靠遥感和GIS结合进行分析.以兰海高速公路为例,运用该系统进行评价,取得了良好的结果.因此,该体系方法可以作为道路生态影响评价和研究的借鉴和参考.     

Review of the effects of in-stream pipeline crossing construction on aquatic ecosystems and examination of Canadian methodologies for impact assessment

Pipeline crossing construction alters river and stream channels, hence may have detrimental effects on aquatic ecosystems. This review examines the effects of crossing construction on fish and fish habitat in rivers and streams, and recommends an approach to monitoring and assessment of impacts associated with these activities. Pipeline crossing construction is shown to not only compromise the integrity of the physical and chemical nature of fish habitat, but also to affect biological habitat (e.g., benthic invertebrates and invertebrate drift), and fish behavior and physiology. Indicators of effect include: water quality (total suspended solids TSS), physical habitat (substrate particle size, channel morphology), benthic invertebrate community structure and drift (abundance, species composition, diversity, standing crop), and fish behavior and physiology (hierarchy, feeding, respiration rate, loss of equilibrium, blood hematocrit and leukocrit levels, heart rate and stroke volume). The Before-After-Control-Impact (BACI) approach, which is often applied in Environmental Effects Monitoring (EEM), is recommended as a basis for impact assessment, as is consideration of site-specific sensitivities, assessment of significance, and cumulative effects.