Methane emission in a rice field of Thailand

ＭｅｔｈａｎｅｅｍｉｓｓｉｏｎｉｎａｒｉｃｅｆｉｅｌｄｏｆＴｈａｉｌａｎｄ￥ＲｏｎｇＸｉａｎｇ；Ｃｈｕｅｎ－ＨｏｗＮｇ（ＥｎｖｉｒｏｎｍｅｎｔａｌＥｎｇｉｎｅｅｒｉｎｇＰｒｏｇｒａｍ，ＳｃｈｏｏｌｏｆＥｎｖｉｒｏｎｍｅｎｔ，ＲｅｓｏｕｒｃｅｓａｎｄＤ...     

不同气氛下燃煤SO2的排放规律研究

在立式管状电加热炉上对合山高硫煤在不同的气氛、温度以及Ca／S比的条件下进行了动态燃烧实验，对收集的气体产物进行了红外光谱分析，并讨论了CO2浓度以及温度等因素对SO2释放的影响。结果表明：不同浓度的CO2气氛对煤燃烧过程中硫的释放以及石灰石的固硫效率有着不同的影响，在高于900℃以后，较之空气气氛下，无论是否存在钙基固硫剂，其它三种02／C02气氛下S02的排放量都比较低，且在不同C02浓度下，温度对S02的排放影响不一致。     

广州市实施二氧化硫排污权交易研究

在排污权交易的理论基础上,借鉴美国二氧化硫排放权交易的政策和方法,设计了一套广州市实施二氧化硫排污权交易的框架,旨在为广州市控制削减二氧化硫排放提供一种基于市场的环境管理手段.     

重金属离子在腐殖酸表面的吸附——类颗粒表面吸附模型

本实验用伏安质子滴定法获得重金属离子(Cu~(2+)、Pb~(2+)、Cd~(2+))在腐殖酸表面吸附的实验数据,并基于这些数据提出重金属离子在腐殖酸表面的络合模型。模型中引入两个实验常数:反应系数α和竞争反应常数K_H。实验结果表明,这两个常数的实验值在一相当宽的起始溶液条件下基本稳定。基于这两个常数而获得的pH相关吸附等温线和实验数据相当符合。模型中采用了由电位滴定得到的腐殖酸表面羧基浓度作为最大表面基团浓度,并对其质子解离常数进行了表面电荷影响的修正。     

二维无压稳定渗流分析的改进方法

人类发展演变过程中,经历了各种各样的地质作用所造成的灾害,其中大部分地质灾害的形成都有地下水的参与,因而确定地质体稳定性时不能忽略地下水。无压渗流是比较复杂的非线性问题,难点在于如何求自由面, 尤其是对溢出点的求解一直没有很好的解决。本文提出了求解无压渗流自由面的一种新方法,在采用等效渗透系数法搜索到自由面后,通过反复移动溢出点再次搜索自由面,最终达到准确求解自由面的目的。实例证明该方法是简单准确有效的。本方法对解决工程问题具有一定的实际意义。     

贵州省万山汞矿区地表水中不同形态汞的空间分布特点

利用两次金汞齐-冷原子荧光光谱法,对贵州省废弃汞矿山万山矿区地表水不同形态汞(活性态、溶解态、颗粒态)的含量进行测定。样品活性态汞为1.04~402 ng／L;溶解态汞为12.5~426 ng／L;颗粒态汞变化很大,最低只有1.38 ng／L,最高达4 427 ng／L。研究表明:(1)直接与矿山冶炼活动排放物炉渣接触的溪流水污染程度最高,总汞高达4.46μg／L;(2)与矿山开采活动排放的废石或贫矿石接触的溪流水污染程度较低;(3)远离汞矿开采、冶炼活动区的地表水总汞接近汞矿化带背景参考值。     

Cobalt in alluvial Egyptian soils as affected by industrial activities

ＩｎｔｒｏｄｕｃｔｉｏｎＩｎｎａｔｕｒｅＣｏｏｃｃｕｒｓｉｎｔｗｏｏｘｉｄａｔｉｏｎｓｔａｔｅｓ ,Ｃｏ2 + ａｎｄＣｏ3+ ,ａｎｄｆｏｒｍａｔｉｏｎｏｆｔｈｅｃｏｍｐｌｅｘａｎｉｏｎＣｏ(ＯＨ) - 3 ｉｓａｌｓｏｐｏｓｓｉｂｌｅ .ＤｕｒｉｎｇｗｅａｔｈｅｒｉｎｇＣｏｉｓｒｅｌａｔｉｖｅｌｙｍｏｂｉｌｅｉｎｏｘｉｄｉｚｉｎｇａｃｉｄｅｎｖｉｒｏｎｍｅｎｔ,ｂｕｔｄｕｅｔｏａｈｉｇｈｓｏｒｐｔｉｏｎｂｙＦｅａｎｄＭｎｏｘｉｄｅｓ,ａｓｗｅｌｌａｓｂｙｃｌａｙｍｉｎｅｒａｌｓ,ｔｈｉｓｍｅｔａｌｄｏｅｓｎｏｔｍ…     

Biogenic VOCs emission inventory development of temperate grassland vegetation in Xilin River basin, Inner Mongolia, China

Given the key role of biogenic volatile organic compounds(VOCs) to tropospheric chemistry and regional air quality, it is important to generate accurateVOCs emission inventories. However, only a less fraction of plant species, in temperate grassland of Inner Mongolia, has been characterized by quantitative measurements. A taxonomic methodology, which assigns VOCs measurements to unmeasured species, is an applicable and inexpensive alternation for extensive VOCs emission survey, although data are needed for additional plant families and genera to further validate the taxonomic approach in grassland vegetation. In this experiment, VOCs emission rates of 178 plant species were measured with a portable photoionization detector( PID). The results showed the most of genera and some families have consistent feature of their VOCs emission, especially for isoprene, and provide the basic premise of taxonomic methodology to develop VOCs emission inventories for temperate grassland. Then, the taxonomic methodology was introduced into assigning emission rate to other 96 species, which no measured emission rates available here. A systematical emission inventory of temperate grassland vegetation in Inner Mongolia was provided and further evidence that taxonomy relationship can serve as a useful guide for generalizing the emissions behavior of many, but not all, plant families and genera to grassland vegetation.     

热液中金的沉淀机理研究综述

金的沉淀机理是了解热液金矿床成矿机制的关键。本文总结了金从热液中沉淀机理的最新研究成果，介绍了各种主要含金配合物的溶解度拨制机制，阐述了矿物表面吸附／还原以及电化学富集等矿物表面作用对金沉淀行为的制约。     

Methods for project-based mechanisms (JI/CDM)—relevance of IPCC inventory guidelines

A baseline for a project consists of estimates of annual emissions of greenhouse gases (GHG) for a given time period without implementing the project. A general three-step process for determining the baseline is suggested. The emission reduction of the project is given by the difference between the baseline and the monitored annual emissions. A preferred method, direct measurement of the emission reduction, is possible for some types of projects. Methods for estimating the annual baseline emissions are not necessary for the latter category, and a definition of this project category is suggested. IPCC Guidelines for National GHG Inventories categorise the emission sources so that only direct emissions from consumption of fuel and feedstock are calculated. There are thus no emission factors for indirect emissions (e.g. electricity consumption or km transported) or emission factors that depend on technology only, independent of consumption of fuel and feedstock. Technology-dependent emission factors may thus need to be developed for estimating indirect emissions and multi-project baselines. Consistency should be sought with the IPCC Guidelines when estimating annual baseline emissions and in monitoring project emissions to ensure comparability with the National Inventories.