上海城市街道峡谷道路绿化模式研究

街道峡谷在上海城市中普遍存在,街道峡谷中污染气体的扩散受到屋顶风向、风速、高宽比、峡谷两侧建筑物的对称性、高度分布和街区形状等因素的影响。文章对适合于不同街道峡谷形式的、较为典型的道路绿化模式进行了研究。结果表明,上海城市街道峡谷中的道路绿化模式可归纳为:梯级递进式、斑块复合式、疏朗开敞式、模纹花镜式和独立行道树式5种。当街道峡谷与主导风垂直:(1)街道峡谷的W/H>5且为平行型峡谷时,绿化模式应采用梯级递进式或疏朗开敞式;(2)街道峡谷的W/H为0.6～5且为平行型峡谷时,绿化模式在迎风侧采用流朗开敞式、背风侧采用模纹花镜式,或者两侧都采用模纹花镜式;(3)街道峡谷的W/H<0.6且为平行型峡谷时,绿化模式应采用模纹花镜式或独立行道树式;(4)街道峡谷的W/H<0.6且为递升型峡谷时,绿化模式在迎风侧采用斑块复合式或模纹花镜式,背风侧采用模纹花镜式或独立行道树式;(5)街道峡谷的W/H<0.6且为递降型峡谷时,绿化模式可采用模纹花镜式或独立行道树式;当街道峡谷与主风向平行:宽、高比大的街道绿化模式应采用梯级递进式或斑块复合式,当街道峡谷的高度是宽度的倍数时,道路绿化宜采用疏朗开敞式或独立行道树式。     

北京城区雨水径流水质及其主要影响因素

掌握城区雨水径流水质及其主要的影响因素是有效地利用城区雨水资源和控制城市非点源污染的基础。根据北京 1998— 2 0 0 0年大量的降雨径流水质数据 ,本文分析了城区屋面和道路雨水径流的水质变化规律及其主要影响因素城市雨水径流的水质很差 ,初期径流的污染程度甚至超过城市污水。除了空气质量的影响外 ,最重要的影响因素是屋面材料、道路类型及路面污染状况、气温、降雨强度、降雨量和降雨间隔时间等     

大气微生物粒子与飘尘粒子的关系

用ＡＮＤＥＲＳＥＮ生物粒子采样器和光散射气溶胶粒子计数器，在北京西单对大气细菌、真菌和飘尘粒子的浓度、粒度分布及它们之间的关系进行了观测和研究。结果表明，大气细菌的粒度是负偏态分布，大气真菌是对数正态分布，飘尘是正偏态分布。大气细菌浓度与飘尘浓度的比值冬季大，为１１９５３８；夏季小，为２４２１７；年平均比值为６７５１７，＞２．０μｍ的菌尘比值为１５２５３８７，２．０μｍ～８．２μｍ的菌尘比值为３３１８，＞８．２μｍ的菌尘比值为３９４。大气真菌浓度与飘尘浓度的比值冬季大，为２１２７７０；夏季小，为６５５８５；年平均比值为１３５３４４，＜２．０μｍ的菌尘比值为９５２６９８，２．０μｍ～８．２μｍ的菌尘比值为５３４３，＞８．２μｍ的菌尘比值为２６３２。     

猫儿山自然保护区生态受益者支付意愿及影响因素

利用问卷调查和条件估值法，以猫儿山自然保护区为例，基于保护区受益者视角，分析受益区居民对保护区的认知、支付意愿及其影响因素和支付方式，探讨自然保护区生态补偿机制的构建。结果表明：（1）受益区居民对猫儿山自然保护区基本情况不熟悉，但绝大多数受益者认同保护区与漓江中下游的水源密切相关。部分受访者不认同作为保护区生态效益受益者的身份；（2）8558%的受益者愿意为猫儿山自然保护区提供帮助，受益者的支付意愿为每户每年28789元，对受益者来说，保护区生态系统服务的经济价值为202×108元/a；（3）文化层次和家庭年收入与支付意愿的关系呈单调变化，职业的影响表现出企业员工的支付意愿最高，其次是教师，农民的支付意愿最低；（4）受益者支付意愿的方式偏好存在差异性，比起现金支付，受益者更倾向于通过参加环保公益活动和纳税的形式，支付保护区提供的生态效益。     

蔬菜与餐厨垃圾厌氧发酵启动阶段微生物分析

为了研究厌氧发酵启动阶段微生物菌群结构、数量变化情况与沼气产量的关系，分别对蔬菜废弃物和餐厨垃圾单一物料发酵进行分析，并测定pH值、挥发性脂肪酸（VFA）、氧化还原电位。结果表明，餐厨垃圾比蔬菜废弃物的启动时间长，但产气持久。蔬菜废弃物中细菌达峰值的时间早于餐厨垃圾，说明蔬菜废弃物中的有机质更利于微生物降解利用。两种原料中的微生物群落结构变化一致，启动阶段初期好氧和兼性厌氧细菌属优势菌，其中产酸菌增殖速率高于氨化细菌，是启动阶段降解有机质的主要菌群。随后厌氧细菌快速增殖，13增殖速率由不足20％增长到近100％并保持稳定。厌氧纤维素降解菌在启动阶段增殖较慢，原料中纤维素降解在厌氧发酵后期。原料液VFA中丁酸含量最多，最高浓度4．7mg／mL以上，占有机酸总量总量的46％以上，厌氧发酵类型为丁酸发酵型。     

Describing the annual cyclic behaviour of Be concentrations in surface air in Oceania

Surface air concentrations of ⁷Be at a number of stations in Oceania show a distinct annual cycle. We apply a sinusoidal model to describe this cycle. The results show that peak ⁷Be concentrations in surface air occur during early spring at tropical latitudes and during mid-to-late summer at middle latitudes. Comparison with available ⁹⁰Sr surface air data for the southern hemisphere indicates that stratosphere-to-troposphere exchange is an active atmospheric process controlling the ⁷Be annual cycle throughout the Oceania region. Vertical transport of air within the troposphere also seems to influence the observed annual cycle. Seasonality in rainfall is not thought to control the annual cyclic behaviour of ⁷Be in surface air.     

植草沟在城市面源污染控制系统的应用

暴雨径流造成的城市面源污染已引起广泛重视,为控制和削减进入受纳水体的径流污染负荷,各种技术措施得到发展,植草沟便是其中之一.植草沟是景观型地表沟渠排水系统,从植草沟定义、类型、设计计算、参数确定、运行维护及应用实例方面作了较详细介绍.植草沟在条件合适时可代替传统的雨水管道,具有很好的推广应用前景.     

Public perception of locally unwanted facilities in Hong Kong: implications for conflict resolution

This paper aims to investigate factors affecting public attitude towards the siting of locally unwanted land uses (LULUs) and to explore the possible strategies to resolve such conflicts. Three questionnaire surveys were undertaken in communities with different siting experiences and socio-economic profiles. Over 750 individuals were successfully interviewed in each study district. The three communities were found to share similar risk beliefs but show variations in the level of awareness of and response to LULUs. In communities with a disproportionate share of LULUs, many residents did not trust the government in handling LULU issues and thought that the siting process was unfair. The results of the binary logistic regression analysis show that people are likely to oppose the siting of a LULU in their community if they have a negative siting experience, do not perceive the need, accord a high risk to the facility and have a low level of trust in government. The resolution strategies preferred by the public are greater public participation and effective mitigation of risks and impacts, rather than provision of compensation and incentives. All these call for policy-makers to be sensitive to local concerns, engage the public in the process, communicate risks effectively and foster trust building.