碎砖骨料再生混凝土配合比研究

用正交法试验分析了碎砖骨料混凝土的配合比，提出水灰比和碎砖骨料掺量分别是影响混凝土强度和流动性的主要因素。倡导用碎砖做混凝土骨料，保护生态环境。     

铝业赤泥免烧砖中试生产及产业化

利用铝厂赤泥、自备电厂粉煤灰、矿山石渣为主要原料在国内第一条赤泥砖生产线上进行了中试生产,采用了自然养护和蒸压养护两种生产工艺。自然养护的赤泥免烧砖达到了非烧结普通粘土砖标准(JCT4221991)(1996)中15级要求,蒸压养护的赤泥免烧砖达到了蒸压灰砂国家标准(GB119451999)中优等品MU15级的要求。通过成本核算,自然养护的赤泥免烧砖的生产成本能够控制在0.11元块以下,蒸压养护的赤泥免烧砖的生产成本能够控制在0.14元块以下,具有较好的经济性。     

居住区地下车库噪声在建筑群间的传播和影响模拟计算

针对城市居住区2种典型的建筑布局,结合随机点声源模型,对居住区内地下车库噪声影响进行了分析计算.通过实测值和预测值的比较,该预测模型精度较好.运用该模型预测规划与新建的居住区地下车库的噪声的影响,可为城市小区建设规划中有效控制噪声污染提供科学依据.     

恶臭假单胞菌Pseudomonas putida 5-x细胞壁膜系统的Cu2+吸附性能

对1株从电镀废水中分离出的革兰氏阴性菌恶臭假单胞菌P.putida 5-x的细胞表面组分对Cu²⁺的吸附性能进行了分析研究.结果表明,分离的P.putida 5-x细胞壁膜的Cu²⁺吸附容量是完整细胞的5倍之多.细胞表面组分如肽聚糖层、细胞外膜和细胞内膜在P.putida 5-x细胞壁膜的Cu²⁺吸附过程中都发挥了作用.肽聚糖层、细胞外膜和内膜在P.putida 5-x细胞壁膜中的含量依次为细胞内膜>外膜>肽聚糖层,而它们的Cu²⁺吸附容量的大小依次为肽聚糖层>外膜>内膜.在P.putida 5-x细胞壁膜对Cu²⁺的吸附过程中,肽聚糖层贡献了不到15%的吸附容量,而细胞外膜和内膜分别贡献了30%～35%和25%～30%.P.putida 5-x细胞外膜中的磷脂含量明显比其它报道的革兰氏阴性细菌的细胞外膜高,这可能是P.putida 5-x细胞外膜具有较高Cu²⁺吸附容量的主要原因,并由此导致P.putida 5-x细胞壁膜的高Cu2+吸附容量.     

控制室内污染发展绿色建筑

本文介绍由于居室装修而导致室内空气污染，论述了治理室内环境污染的途径，及绿色建筑是建筑业的发展方向。     

深入认识生态承载力的空间构成发展节约化畜牧业的初探

内蒙古自治区位于祖国北部边疆，地域辽阔，是我国北疆的绿色屏障，由于自然条件的制约，草场保护与草地资源利用间的矛盾比较突出。近几年我区的过度放牧和养殖，使草地面积退化，而且草地建设严重滞后。我区有得天独厚的风能和水资源，但资源分布不均，东部地区水资源和草地资源丰富，而中西部地区风能资源丰富，如何充分认识与利用资源空间有机组成，充分利用生态承载力，实现生存与生态良性发展，则显得十分重要。本文要结合我区的风、水、土、草等资源的分布条件，探讨我区走协调发展的道路。     

九江-瑞昌5.7级地震现场房屋安全性鉴定工作的探讨

九江-瑞昌地震虽然震级较小,但震源深度浅,加之本地为历史少震地区,设防水准低,量大面广的非标准砖混和砖木房屋破坏较严重,造成13人死亡和多达20亿的直接经济损失.这充分暴露出我国少震地区城市防御力不足的弊端,经济发展的同时更应注意地震灾害风险的规避.本文介绍了本次地震现场应急工作情况,例举了地震区内不同结构类型房屋在这次地震中的表现和震害特点,并根据本次地震现场房屋安全性鉴定工作的实践和多次地震现场应急工作的经验,对本次地震现场应急工作进行总结.     

阜新市城区大气环境容量核算结果及其应用

根据大量模式化参数，通过核算，得出了阜新市城区普通空气污染物的环境容量，给出了城区各分区及每个网格的分解量，应用这些成果，将对老污染源及新工业项目的环境管理，发挥极其重要的作用，对阜新市的可持续发展战略有着重要意义。     

Some Lessons Learned from Public Health on the Process of Adaptation

Lessons learned from more than 150 years of public health research and intervention can provide insights to guide public health professionals and institutions as they design and implement specific strategies, policies, and measures to increase resilience to climate variability and change. This paper identifies both some modifications to public health systems that may enhance adaptive capacity, and lessons drawn from the history of managing environmental and other threats in the public health sector that may have relevance for other sectors as they design approaches to increase their adaptive capacity to more effectively cope with climate variability and change. The views expressed are the author’s own and do not represent official US EPA policy.     

Carbon Dioxide Balance of Wood Substitution: Comparing Concrete- and Wood-Framed Buildings

In this study a method is suggested to compare the net carbon dioxide (CO₂) emission from the construction of concrete- and wood-framed buildings. The method is then applied to two buildings in Sweden and Finland constructed with wood frames, compared with functionally equivalent buildings constructed with concrete frames. Carbon accounting includes: emissions due to fossil fuel use in the production of building materials; the replacement of fossil fuels by biomass residues from logging, wood processing, construction and demolition; carbon stock changes in forests and buildings; and cement process reactions. The results show that wood-framed construction requires less energy, and emits less CO₂ to the atmosphere, than concrete-framed construction. The lifecycle emission difference between the wood- and concrete-framed buildings ranges from 30 to 130 kg C per m² of floor area. Hence, a net reduction of CO₂ emission can be obtained by increasing the proportion of wood-based building materials, relative to concrete materials. The benefits would be greatest if the biomass residues resulting from the production of the wood building materials were fully used in energy supply systems. The carbon mitigation efficiency, expressed in terms of biomass used per unit of reduced carbon emission, is considerably better if the wood is used to replace concrete building material than if the wood is used directly as biofuel.