生态文明与农业发展

农业作为国民经济的基础,是生态文明的重要内容,其文明程度直接体现生态文明程度.生态文明建设给农业经营提出了更高的要求,也为农业生产的发展指明了方向.充分认识生态文明建设与农业生产的关系,加强农业相关人员的生态文明教育和农业环保法制建设,实施更加科学、文明的农业经营方式将对促进农业的可持续发展和生态文明建设发挥积极的作用.     

生态校园建设现状分析

生态校园建设的类型主要有:景观园林设计型、生态技术型、教育管理型.通过在校园内建立生态环境体系,使校园内有限的资源得到循环、合理、科学的使用,提高学校生态环境质量.     

生态环境监理——天津市大港区的探索

环境保护包括污染防治和生态保护两大方面 ,目前 ,在污染源治理取得明显效果 ,生态环境遭受不同程度破坏的情况下 ,实施生态环境监理势在必行。大港区环保局就生态环境监理开展了探索性的工作。     

满洲里市景观生态修复与重建

受到自然和人为因素的影响,满洲里市生态环境十分脆弱。其基本景观型包括城镇、水域、垦殖地和矿区景观。根据各类景观破坏的原因和现状,将产业生态学与流域生态学的原理相结合,提出重建、修复的措施或对策。     

可持续发展与技术创新

加强技术创新 ,大力发展高新技术产业 ,有利于我国可持续发展战略实施。本文阐述了技术创新对提高综合国力竞争、调整产业结构的作用 ,分析了我国技术创新系统存在的问题 ,提出了技术创新及其实现产业化的政策选择。     

西部地区加快开发应当克服“资源近视症”

本文从分析我国传统的经济增长方式入手,通过对资源近视症”的表现及后果的分析,提出西部西地区,特别是西部少数民族地区只有树立全面的资源观,立足优势,面向市场,抓住机遇,合理开发资源和利用资源,才能走出一条符合本民族,本地区实际的可持续发展之路。     

陇南长江流域经济发展和生态重建战略研究

陇南长江流域大多地处嘉陵江上游的源头地区,是一个资源较为富集但经济相对落后、生态环境脆弱且人口压力较大的丘陵山区。本文从可持续发展的角度出发,着眼世纪之交摆脱贫困与奔向小康转换时期经济发展和生态重建的协调演进,提出产业结构调整的基本思路是立足山区优势发展特色农业,市场配置资源、培植支柱工业,商贸、旅游并举、突出第三产业、强化基础设计、增强发展后劲;空间结构重组的战略构想是重点发展东部经８济重心区、     

生态恢复过程中的种群遗传学考虑

生态恢复是生态科学的最终实验,从种群角度看,恢复的目标是使种群（尤其是优势种或建群种）到具有生长、繁殖和适应进化变化的能力。要达到这个目标,种群遗传学知识必不可少。遗传变异是物种适应变化环境的基础,而局部适应则是种群适应局部环境遗传分化的结果,它们在生态恢复中起着重要的作用。分析了生态恢复过程中影响种群遗传变异因素,主要有取样误差和小种群效应（主要是瓶颈或建立者事件及其以后的近交和漂变等）,在进行     

可持续发展的生态学思考

本文从生态学角度对可持续发展理论进行了思考。指出生态危机是可持续发展产生的基本背景;生态学中许多基本理论,如协调、适应、稳定、有序、循环再生及生态系统理论等,是可持续发展不断完善的理论基础;包括生态规划、生态技术与生态管理在内的广义生态工程,是实现可持续发展的有效途径     

An Assessment of the Ecological Condition of Long Island Sound, 1990–1993

Data from the Environmental Protection Agency's (EPA) Environmental Monitoring and Assessment Program (EMAP) from 1990 to 1993 were used to assess the condition of the Long Island Sound (LIS) estuary. Ambient water, sediment and biota were collected during the summer months from 53 LIS stations using an unbiased sampling design. The design consists of two LIS subunits, LIS proper, and small estuaries (<2.6 km2) at the margins of the Sound. Selected indicators of condition included: benthic species composition, abundance and biomass; fish species composition and gross external pathology; sediment physical and chemical characterization and sediment toxicity; and water clarity and quality. Results of the four-year sampling indicated that 28(±11)% of the areal extent of LIS proper had a benthic index < zero (impacted) and 51(±12)% of the area of small estuaries was impacted. Analysis of the results of other indicators also shows that small estuaries were particularly affected. For example, 42(±10)% of the areal extent of small estuaries exhibited sediment toxicity, and significant chemical contamination was evident in 22% of the area of small estuaries. Low dissolved oxygen (D.O.) concentrations (<5 ppm), however, appeared to affect only the deeper open waters of western LIS. Approximately 48(±12)% of the areal extent of LIS proper documented exposure to at least moderate D.O. stress (<5 ppm). The overall results of this monitoring study indicate that significant anthropogenic impacts have occurred in LIS and that if remediation was to take place, specific localized sediment problems would need attention. Point source and non-point source nutrient inputs to the Sound, which are believed to be the primary causative factor for the observed hypoxic conditions, would also need attention.