低山丘陵区水土保持治理与生态环境效应

分析了低山丘陵区水土流失等级分布，水土流失的形成原因及危害，指出低山丘陵区水土流失综合治理要以小流域综合治理为主，阐明小流域水土流失的规律性，以及根据小流域3个地貌单元类型按“三条带”模式进行综合治理：山顶林草防治、山腰经济林带整治、山脚坡改梯治理的技术措施，着重论述综合治理的生态环境效应：明显地保水保土保肥，在降雨量相同的情况下等高种植、坡改梯、封山育林雨强明显小于坡耕地，起始产流时间延迟，径流量减少近2/3，土壤侵蚀量明显比坡耕地少得多。土壤侵蚀携带养分，坡耕地损失量最大，等高种植全氮、全磷的损失量最小；坡改梯有机质、有效氮、速效钾流失量较少，说明坡改梯的保肥效果优于等高种植。林草植被对改善生态系统的环境效应和提高生物多样性功能，为低山丘陵区生态环境恢复和农业可持发展奠定基础。     

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。     

VR-GIS技术在小城镇洪水淹没模拟分析中的应用

近年来利用计算机和信息技术研究洪水灾害是个研究热点,但小城镇在防洪减灾方面缺少应有的关注和重视。本文对VR(虚拟现实技术)-GIS技术在小城镇洪水淹没模拟分析中的应用进行了研究,解决了系统实现过程中的一系列关键技术:小城镇空间数据库的建库技术及三维可视化、洪水淹没范围的确定,以及洪水淹没实时动态演示等问题。该技术已在国家十五科技攻关项目所开发的《小城镇基础设施防灾减灾决策支持系统》中得以实现。实践证明:小城镇空间数据库的建库技术速度快、成本低,适合中国小城镇的信息化现状。利用淹没范围的近似计算模型,可以有效迅速准确地计算出洪水淹没范围,有利于防洪减灾的迅速决策,且偏于安全。小城镇洪水灾害的三维可视化模拟,可以实时动态地演示小城镇遭受洪灾实况的全过程。     

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.     

民营中小企业安全文化建设探讨

企业安全文化建设对于企业安全管理起着至关重要的作用,民营中小企业作为我国经济体系的生力军,其安全管理工作必须注入新的安全管理理念、理论和方法。分析了民营中小企业安全文化建设的制约因素,在基于"本质安全、目标统一和全员参与"三个原则的基础上,初步构建由观念文化、制度文化、行为文化和物态文化四部分组成的民营中小企业安全文化建设框架,并提出相应的建设方法,对于民营中小企业的安全发展有着极其重要的意义。     

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.