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。     

中国“达标排放”政策的实证分析及理论探讨

以固定点源烟尘排放为例,从排放标准和监测标准两方面讨论了中国现阶段“达标排放”的状况,指出当前的大气污染源达标排放实际上是“初步达标排放”,现在的排放标准和监测规范合适考核污染源的初步达标排放,不适合考核污染源的连续达标排放。排放标准的规定形式、监测规范和适用范围需要改革。现在的排放标准指标需要与监测规范和超标率限值结合起来,以促进污染源的连续达标排放。     

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.     

论中国金矿床成矿时代特点

中国金矿床成矿时代特点可以概括为“一老一新成矿 ,东西南北有别”。“一老一新成矿”表现为主要成矿时代为早元古代 (2 6 0 0～ 14 0 0Ma)和中生代 (部分晚古生代 30 0～ 10 0Ma) ,且中生代形成的金矿床所占的比例更大。“南北有别”表现为 :我国早期成矿作用在扬子地块和华南地区主要以中元古代 (180 0～ 14 0 0Ma)为主 ,而华北地区以早元古代 (2 6 0 0～ 180 0Ma)为主 ,甚至存在晚太古代的金矿床 ;我国晚期成矿作用在华南地区以印支期—燕山早期为主 (如海南—粤西地区为 2 30～ 190Ma) ,在华北、胶东地区为燕山中晚期 (14 0～10 0Ma)。“东西有别”表现为我国东部地区中生代是金矿床成矿的最重要时期 ,而西部地区晚古生代是金矿床成矿的重要时期 (以北山、天山和北疆地区最明显 ,成矿年龄以 30 0～ 2 30Ma为主 )。同时 ,我国的金矿床普遍具有“成矿物质来源老 ,矿床定位年龄新”、“多期成矿作用叠加明显”和以“岩浆热液型为主”的特征。上述特征是受中国独特的大地构造及其演化历史所控制的。     

华南玄武岩红土化过程中微量元素地球化学

广东、海南的玄武岩．在强烈的红土化过程中．元素在红土剖面中发生迁移和残留、贫化和富集。根据红土化过程中元素的地球化学性状，将元素划分为活泼元素和不活泼元素两大类。并首次采用了元素它集因子这个概念来探讨红土化过程中微量元素的地球化学行为。最后讨论了红土化过程小金的表生富集作用。     

中国东南大陆中生代火山岩带的火山岩相类型

本文根据岩浆作用的表现形式、火山喷发方式、搬运方式、堆积环境、成岩过程以及距火山口远近等因素，将岩浆作用产物的岩相类型分为侵入岩相、侵出岩相、火山岩相等三大类十二种岩相类型．并详细阐述了区内火山岩相类型及其时间分布特征。     

中国水资源短缺地域差异研究

论文以人均水资源量、单位面积水资源量、人均供水量和单位GDP占有水资源量为指标,采用综合评价方法对全国各省、自治区、直辖市(除台湾外)进行缺水程度及缺水类型的划分。根据缺水综合指数划分为丰富区、脆弱区、缺水区和严重缺水区;根据人均水资源量、单位面积水资源量、人均供水量与全国均值的差值划分为资源型、工程型和过载型。     

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.     

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.     

刍议排污权价格的合理界定

排污权交易在中国的试点过程中,显现了强大的生命力,然而,由于对排污权交易基础理论理解的偏差,导致了实践层面上的缺陷,如排污权初始分配是否应该有偿的问题;排污权商品再分配价格应不应该包括正的外部效应价值问题;在排污权交易制度改革与中国其他制度的改革(现行税制改革、绿色GDP的推行)进行中出现的不协调的问题.