处理污水后陶粒作为栽培基质的试验

以秸秆-粉煤灰陶粒（比表面积为7．925m2·g-1）作为曝气生物滤池（BAF）载体填料,处理城市污水和餐饮废水,其COD、NH3-N和TP去除率分别为90．33％、77．44％、82．41％和86．50％、68．98％、80．30％。对处理污水后陶粒的农用资源化可行性进行评估,考察陶粒不同施用量对小白菜（Brassicachinensis）种子萌发、生长状况和产量的影响。结果表明,处理污水后陶粒的性能指标达到GB8172—87《城镇垃圾农用标准》;陶粒质量分数为20％时小白菜种子发芽率最高,且萌发较快,在5d时达到100％;随陶粒施用量增加,小白菜长势更好,产量大致呈增加趋势,陶粒质量分数为80％时增产率最高,为352．51％。但陶粒施用量越高,栽培基质抗干旱能力越差,陶粒质量分数为20％和40％处理具有较好的土壤保湿效果。     

不同堆料比对石油烃废弃物堆肥处理效率的影响

采用高温好氧堆肥化技术,研究了不同堆料比对石油烃废弃物堆肥处理效率的影响。实验设计难度降解有机物／易降解有机物（堆料比）分别为１：１１、１：３０和１：６０,结果表明：１：３０为最适堆料比,在这一条件下,废弃物中的石油烃经２８ｄ堆肥处理可达到５９．１２％的去除率。     

城市物质流分析框架及测算方法

在借鉴国家物质流分析(MFA)框架基础上,针对进出城市系统的物质数据缺乏且难以统计的特点,引入面向元素或产品的物质流分析(SFA)要素,建立了城市尺度物质流分析框架.与国家物质流分析相比,该框架总体结构和物质分类上相同,但输入量、净存量和输出量的计算顺序和假设条件不同.对于化石能源,可由城市统计年鉴中的能源平衡表直接得出本地开采量、净存量、调入量和调出量;对于生物质,本地开采(生产)量一般都有统计,净存量可通过假设人均消费量相对稳定估算得出,而调入量和调出量则需要对大宗工业用途进行调查并做少量假设计算得出;对于金属矿物及其产品、工业非金属矿物及其产品、建筑材料3类物质,本地开采量和消费量一般都有所统计,而调入量和调出量的计算则需要首先采用针对元素或成品的物质流分析来获取城市系统中的净存量,然后再配合生产和消费数据并做少量假设测算得出.其他项目的获取或测算同国家物质流分析,由此得到的城市物质流分析框架可以用于城市间物质代谢的比较.      

固定污染源废气监测用挥发性卤代烃标准气体制备不确定度研究

针对固定污染源挥发性卤代烃污染物的排放监测需求,采用称量法制备固定污染源废气监测用挥发性卤代烃标准气体(各组分具有浓度差异),并开展制备不确定度评定研究。通过分析原料试剂纯度、液态/气态组分称量、混合液配比、摩尔质量、气体残留等因素和环节引入的不确定度,确立标准气体制备不确定度评定流程。最终,确定固定污染源废气监测用挥发性卤代烃标准气体制备过程引入的相对扩展不确定度(k=2)小于1%。液态/气态组分称量和上一级中间气浓度引入的不确定度对特性量值不确定度的贡献较大,原料试剂纯度对不确定度的影响较小,摩尔质量和气体残留对不确定度的影响可忽略。     

牡丹皮、川芎和石菖蒲挥发油提取工艺研究

目的确定牡丹皮、川芎和石菖蒲挥发油最适宜的提取工艺方法．方法用共水回流冷凝法研究了三种药材混合提取及分开提取挥发油的工艺方法,以挥发油的重量为指标来评价提取工艺．结果混合提取及分开提取所获得的挥发油的重量,经统计学分析无显著性差异（P〉0．05）．结论共水回流冷凝法混合提取牡丹皮、川芎和石菖蒲挥发油的工艺可行、简便,适合工业化大生产．表5,参3     

高校市场废弃物物流发展问题探析

高校市场中存在着废弃物物流活动,需要从学校、环境、社会等角度对其废弃物物流体系进行改进,创建高校市场废弃物绿色物流回收系统．通过分析高校市场废弃物物流现状和存在问题,从学校、企业和政府等方面提出创建高校市场废弃物物流回收系统的诸多措施．图1,参5．     

Removal of basic fuchsin dye from aqueous solutions using graphite oxide modified aromatic polyurethane foam material

Graphite oxide modified polyurethane foam (GO/PUF) was used for adsorption of basic fuchsin from aqueous solution and adsorption conditions were optimized to attain an efficiency of 99.5%. The adsorption isotherm was in agreement with the Langmuir model. Kinetic study followed pseudo-second order. Determination of Gibbs free energy and enthalpy change of adsorption indicated spontaneous and endothermic adsorption behavior, suggesting that the adsorbent had a potential for the removal of dyes from industrial wastewater.     

不同粒径和不同浓度清洁疏浚物对2种海洋微藻生长的影响

采用室内模拟试验研究了不同粒径和不同浓度悬浮清洁疏浚物对2种常见海洋微藻小球藻（Chlorella sp.）和新月菱形藻（Nitzschia closterium）生长的影响.结果表明,在8d的试验周期里,与对照组相比,不同浓度清洁疏浚物对2种海洋微藻生长的影响均达极显著水平（P＜0.01）.在相同粒径范围内,悬浮清洁疏浚物质量浓度为1～7g·L-1时,其对微藻生长的抑制作用随浓度升高而增加.随悬浮清洁疏浚物粒径的减小,2种海洋微藻的细胞密度呈下降趋势,＞88～ 125 μm粒径范围内生长的藻细胞受影响最小,0～16 μm粒径范围内生长的藻细胞受影响最大.悬浮清洁疏浚物对2种海洋微藻比生长速率的抑制作用明显,延缓了最大比生长速率出现的时间.2种海洋微藻对悬浮清洁疏浚物的敏感性存在差异,小球藻对悬浮清洁疏浚物的反应更加迅速.     

Eco-efficiency of urban material metabolism: a case study in Xiamen,China

In this research, the data envelopment analysis (DEA) model of measuring the eco-efficiency of urban material metabolism has been constructed based on the urban material input and output indicators. According to the data of Xiamen from 1985 to 2007, an empirical study was conducted to measure the eco-efficiency of urban material metabolism using DEA program. The results showed a general downtrend of Xiamen's eco-efficiency of material metabolism from 1985 to 2007, in which there were 15 efficient years and eight inefficient years. The eco-efficiency and urbanization rate of Xiamen was remarkably negatively correlated. Moreover, the results revealed at 4 years (1995, 2001, 2002 and 2003) there had been undesirable output slack (environmental pollution), and at 2 years (1991 and 1999) there had been desirable output slack (GDP), and at 8 years there had been input slack (water, land, food and energy), especially for water and energy. Finally, some suggestions on promoting the eco-efficiency of urban material metabolism were put forward.     

Clustering economic sectors in China on a life cycle basis to achieve environmental sustainability

To improve material efficiency, industrial structure optimization becomes a focal point in Chinese industrial and environmental policies. It is crucial to cluster economic sectors and determine their priority for industrial and environmental policy implementation. Integrating a set of criteria, a hybrid input-output model and the hierarchical cluster analysis, this study clusters China’s economic sectors and determines their priority on a life cycle basis. China’s economic sectors are clustered into three clusters. Industrial structure changes (industrial policy) should encourage the development of sectors in cluster 1 and limit the development of sectors in cluster 2. Technology development and materials recycling (two environmental policies) should mainly focus on sectors in clusters 1 and 2. Future industrial policies in China should limit the development of two sectors named Manufacture of metal products and Extraction of petroleum and natural gas. Instead of limiting some industries by command-and-control, the best policy option is to remedy environmental standards and law enforcement. Enterprises belonging to the identified key sectors from the viewpoint of direct production impacts should be concerned to achieve enterprise sustainability. To achieve sustainable production chains, the identified key sectors from the viewpoint of accumulative production impacts should be concerned. For sustainable consumption, the identified key sectors from the viewpoint of consumption impacts should be concerned to transform consumption styles. Most of environmental pressure can be alleviated not only by technical improvements and material recycling, but also by the development of economic sectors in cluster 1.