东风水库九溪河流域面源污染及其防治

由于农药化肥施用量大、水土流失加重，农村生活水污染等原因，九溪河水质呈恶化趋势进而影响东风水库。应采取行政手段与科技措施、治标与治本、短期与长期、重点与综合相结合的办法，控制污染，改善水质。     

Diets of periphytonic invertebrates in a small river

Potential food accessibility in the periphyton has been estimated, and diets of 13 invertebrate species typical of lithorheophilic biocenoses have been compared. Factors responsible for spatial heterogeneity in the composition of food consumed by invertebrates are discussed with special regard to consumption of algae.     

大坝拦截对河流水溶解组分化学组成的影响分析——以夏季乌江渡水库为例

以乌江渡水库为主要研究对象，揭示了大坝拦截条件下的夏季水化学特征：阴离子以HCO-3,SO2-4为主，阳离子以Ca2+,Mg2+为主，其余离子含量低于10%，说明了碳酸盐岩的风化对水体化学组成起到了主要控制作用，蒸发盐岩石的风化对水体化学组成影响较小。水库水体存在温度分层现象，形成了不同层位的水体有着不同的水化学组成，即水化学分层。水化学的分层形成了溶解组分在水库垂直深度上的规律分布，比如受藻类的影响，Si和叶绿素随深度成相反的变化特征；HCO-3受光合作用和有机质降解的影响，30 m 以上随着水深的增加而递增，30 m 以下呈现相反趋势；水库泄水方式明显改变了水化学各种参数和离子在水体中的分配。乌江水库两主要支流（息烽河和偏岩河）分别对乌江渡坝前水体中的Ca2+,SO2-4,HCO-3,Mg2+和K+,Na+,Cl-有贡献。网箱养鱼、生活污水、农业施肥、酸性矿山废水以及酸雨沉降都会对水体造成不同程度的污染。     

全球可持续发展与国际合作

本文认为环境生态是全球可持续发展的重要组成部分,必须在全球范围内,通过有效的国际合作和国际协调来加以解决。作者认为:国际合作应在国际性河流流域管理方面发挥重要作用。对全球温室效应问题,国际组织应重视科学研究,协调各国政府在能源税收、补贴和开发再生能源方面取得进展。此外,在保护地球生物多样性方面,国际组织可调试债务与自然环境互换机制。     

从河流网系整体出发开发整治长江流域

长江是我国最大的河流,干流长6300km,流域面积180万 km~2,占全国国土面积的1/5。整个流域大部分位于湿润亚热带地区,具有丰富的自然资源,工农业产值占全国的45%,是我国最发达的地区。但流域内地区发展很不平衡,下游地区的发展超过中游和上游,干流沿岸城市的发展超过丘陵山区。因此,从河流网系整体出发,均衡开发长江流域很有必要。     

EFFECTS OF ADVANCED WASTEWATER TREATMENT ON THE QUALITY OF WHITE RIVER,INDIANA1

ABSTRACT: In 1983, the City of Indianapolis, Indiana, completed construction of advanced wastewater treatment (AWT) systems to enlarge and upgrade its existing Belmont Road and South port Road secondary treatment plants. A nonparametric statistical procedure, a modified form of the Wilcoxon-Mann-Whitney rank-sum test, was used to test for trends in water quality at two upstream and two downstream sites on White River and at the two treatment plants. Results comparing the pre- (1978–1980) and post- (1983–1986) AWT periods show statistically significant improvements in the quality of the treated effluent and of the White River downstream from the plants. Water quality at sites upstream from the city was relatively constant during the period of study. Total ammonia (as N) decreased 14.6 mg/L and BOD₅ (five-day biochemical oxygen demand) decreased 10 to 19 mg/L in the two effluents. Total ammonia in the river downstream from the plants decreased 0.8 to 1.9 mg/L and BOD₅ decreased 2.3 to 2.5 mg/L. Nitrate (as N) increased 14.5 mg/L in the plant effluents and 2.0 to 2.4 mg/L in the river because of in-plant nitrification. Dissolved oxygen concentration in the river increased about 3 mg/L because of reduced oxygen demand for nitrification and biochemical oxidation processes.     

基于MIKE 21的长江江山制药排污口水环境影响分析——以江山制药公司污水处理站为例

为分析长江沿岸入河排污口设置对水环境的影响,采用MIKE 21建立了长江马鞍山-高桥段二维非稳态水量水质模型,并以江山制药公司污水处理站为例,对其排污口迁址改建前后的水环境影响进行模拟.结果 表明,较于原排污口排放,拟设排污口在执行新排放标准情况下,对九圩港入江断面水质有改善作用,COD、NH3-N、TP的改善率分别为...     

人工曝气复氧整治污染河流

向受到严重有机污染的河流充入溶解氧可以有效消除水体的黑臭,改善水质和恢复生态平衡。文章总结了纯氧增氧系统、鼓风机———微孔布气管曝气系统、叶轮吸气推流式曝气器和水下射流曝气设备等多种使用于河道人工曝气复氧的技术;并列举大量国内外的相关工程实例说明这些技术在实践中的有效性。     

多泥沙河流水质模型研究

针对黄河泥沙含量大、泥沙对河流CODMn浓度影响大的突出特点,运用模拟实验方法,探讨了泥沙对CODMn浓度的影响,揭示了浑水、清水中CODMn浓度与含沙量间的关系.研究表明,黄河浑水中CODMn浓度随含沙量增大呈显著上升趋势,而去除泥沙后清水CODMn浓度测定值随其原含沙量增大呈微上升趋势.依据质量平衡原理,建立了充分考虑泥沙影响的CODMn衰减经验模型.清水中CODMn浓度的变化采用完全混合反应器概念来模拟,浑水中CODMn浓度通过清水中CODMn浓度与泥沙中CODMn浓度之和来量化.模型基本方程的求解采用稳态解析解.模型中的参数通过利用实际监测数据及室内实验结果与优化结合的方法确定.同时,利用实际监测数据对参数和模型进行检验.结果表明,模型结构合理,参数取值可靠,模型精度较好.模型既能揭示汇流区间人为污染对河段水质的影响,又可以反映作为面污染源的黄河泥沙对污染的影响,可作为水质预测的实用工具及规划管理的依据.     

Diverging response patterns of terrestrial and aquatic species to hydromorphological restoration

Although experiences with ecological restoration continue to accumulate, the effectiveness of restoration for biota remains debated. We complemented a traditional taxonomic analysis approach with information on 56 species traits to uncover the responses of 3 aquatic (fish, macroinvertebrates, macrophytes) and 2 terrestrial (carabid beetles, floodplain vegetation) biotic groups to 43 hydromorphological river restoration projects in Germany. All taxonomic groups responded positively to restoration, as shown by increased taxonomic richness (10–164%) and trait diversity (habitat, dispersal and mobility, size, form, life history, and feeding groups) (15–120%). Responses, however, were stronger for terrestrial than aquatic biota, and, contrary to our expectation, taxonomic responses were stronger than those of traits. Nevertheless, trait analysis provided mechanistic insights into the drivers of community change following restoration. Trait analysis for terrestrial biota indicated restoration success was likely enhanced by lateral connectivity and reestablishment of dynamic processes in the floodplain. The weaker response of aquatic biota suggests recovery was hindered by the persistence of stressors in the aquatic environment, such as degraded water quality, dispersal constraints, and insufficient hydromorphological change. Therefore, river restoration requires combined local- and regional-scale approaches to maximize the response of both aquatic and terrestrial organisms. Due to the contrasting responses of aquatic and terrestrial biota, the planning and assessment of river restoration outcomes should consider effects on both components of riverine landscapes.