中国沙尘气溶胶的间接辐射强迫与气候效应

利用在线耦合的区域气候化学模式系统(RegCCMS),对2003~2007年的3,4,5月中国沙尘气溶胶的空间分布,间接辐射强迫和间接气候效应进行模拟.结果表明:沙尘分布主要集中在中国西北的新疆、内蒙、甘肃等地区.5月份最高的中心值浓度达到3500μg/m3,3个月地面浓度依次增大.3,4,5月由沙尘气溶胶造成的第一间接辐射强迫平均值分别为-1.26,-2.0,-2.69W/m2.局部地区达到-7W/m2.考虑到沙尘气溶胶的第一间接气候效应后,使近地面气温下降,降水减少,3,4,5月地面气温变化的平均值为-0.05,-0.07,-0.08K. 3,4,5月降水变化平均值分别为-0.0037,-0.037,-0.1mm/d. 不同的月份和地区,温度和降水的变化存在明显的差异.     

微生物浸出低品位氧化物型镍钴矿研究新进展

微生物浸出技术是处理低品位矿石的有效措施。但目前我国主要针对硫化矿的自养微生物浸出进行研发,而对异养微生物浸出氧化型矿石研究很少。异养微生物可通过其产生的代谢产物的酸解、还原、碱解及络合作用来提取或者溶解低品位氧化物型镍钴矿中的镍、钴金属,有助于解决目前我国镍钴资源短缺及为重金属污染治理提供技术方法。本文针对低品位氧化型镍钴矿、风化壳、以及冶金渣、废电池、废催化剂等二次资源,介绍了世界镍钴资源的现状和低品位氧化物型镍钴矿的资源类型,对异养微生物浸出低品位氧化物型镍钴矿研究现状进行了剖析,指出了异养微生物冶金的主要浸矿条件和存在难题,提出了氧化物型镍钴矿微生物浸取的研究方向。     

电导率温度校正计算方法的改进

通过实验，用分段函数较精确的表示出温度校正系数与温度的关系，对现行电导率温度校正公式进行了改进，可以简化测量过程，提高计算精度。     

不同有机质含量的土壤中DDT对小麦根系的生物有效性

对不同有机质含量的土壤中，分别选用水、正己烷、正己烷／丙酮混合溶剂作为DDT的提取剂，用这3种提取剂逐级连续提取，研究了这3级提取剂所提取的DDT量的差别及其与小麦根吸收的关系。结果表明，有机氯的水提取量随土壤D0c的增加而上升，正己烷提取量随土壤TOC的增加而下降，正己烷／丙酮提取量随土壤TOC的增加而上升。根吸收与水提取量没有确定的关系，但与正己烷提取量具正相关关系，与正己烷／丙酮提取量有负相关关系。     

固相萃取净化气相色谱法快速测定土壤中的氯氰菊酯残留

本文介绍了一种氯氰菊酯在土壤中残留量分析方法.选用硅胶微量柱固相萃取和气相色谱电子捕获检测器定量分析.该方法简便,能够在较短时间内处理大量作品,最低检出浓度为0.0375mg·kg~(-1),回收率在82.91%以上.     

大气混杂污染物诱导8—羟基脱氧鸟苷的形成及机理

以DNA加合物8－羟基脱氧鸟苷（8－OHdG)作为DNA氧化损伤的生物学标志物，用高压液相色谱－电化学检测（HPLC－EC）法对大气混杂污染物染毒后的DNA中8－OHdG进行定量检测，通过气质联用法（GC－MS）进行有机成分分析和原子吸收法（AAS）对其进行无机元素分析，并从大混杂污染物化学组成成分的角度推理并证实了其造成DNA损伤的分子机理。     

生态影响评价中生境评价方法

生态影响评价是环境影响评价的重要分支，生境评价方法是生态影响证件 主要方法。美国是较早开展生态影响评价的国家，发展了一批生境评价方法。本文系统介绍了美国两种最常用的生境评价方法－生境评价系统和生境评价程序，并简要对比介绍其它方法，为我国开展生态影响评价提供一定理论参考。     

Decolorization of mono-azo dyes in wastewater by advanced oxidation process: A case study of acid red 1 and acid yellow 23

Advanced Oxidation Processes (AOPs) have been used as emerging wastewater treatment technologies which can effectively handle various hazardous organics in wastewater and groundwater. The photooxidation of two non-biodegradable azo dyes, acid red 1 and acid yellow 23, were studied in an UV/hydrogen peroxide photochemical reactor with a 5 kW low pressure mercury lamp. It was observed that the decomposition of both azo dyes were pseudo-first order reactions with respect to the azo dye concentrations. Simultaneously, the effects of hydrogen peroxide dosage, pH, initial concentration of the azo dyes and intensity of UV light were also studied. Moreover, the time required for the 50% removal of azo dyes and observed pseudo-first order rate constants were used as parameters to show the efficiency of azo dye treatment.     

Influences of excessive Cu on photosynthesis and growth in ectomycorrhizal Pinus sylvestris seedlings

Growth and photosynthesis responses were measured for Scots pine( Pinus sylvestris L. cv. ) inoculated with ectomycorrhizal fungi ( Suillus bovinus ) under 6.5 and 25 mg/L Cu treatments to evaluate ectomycorrhizal seedlings‘ tolerance to heavy metal stress. Results showed that excessive Cu can significantly impair the growth and photosynthesis of pine seedlings, but such impairment is much smaller to the ectomycorrhizal seedlings. Under 25mg/L Cu treatment, the dry weight of ectomycorrhizal seedlings is 25% lower than the control in contrary to 53% of the non-mycorrhizal seedlings, and the fresh weight of ectomycorrhizal roots was significantly higher than those of non-mycorrhizal roots, about 25% and 42% higher at 6.5 and 25 mg/L Cu treatments respectively. Furthermore,ectomycorrhizal fungi induced remarkable difference in the growth rate and pigment content of seedlings under excessive Cu stress. At 2.5 mg/L Cu, the contents of total chlorophyll, chlorophyll-a and chlorophyll-b were 30% higher in ectomycorrhizal plants than those in non-mycorrhizal plants. O2 evolution and electron transport of PSI and PSII were restrained by elevated Cu stress. However, no significant improvement was observed in reducing the physiological restraining in ectomycorrhizal seedlings over the non-mycorrhizal ones.     

苏南太湖地区水资源价值补偿对物价水平的影响研究

对水资源进行价值补偿是解决我国现阶段水资源短缺和水污染问题的重要手段之一,解决好水资源价值补偿问题是实现资源,环境、社会可持续发展的前提。实施水资源价值补偿政策可能导致的物价水平上升是关系到人民群众生活稳定的重要问题。在实施水资源价值补偿政策之前,对实施这一政策可能引起的物价上涨幅度进行定量分析是十分必要的。本文运用投入产出模型计算苏南太胡地区水资源价值按一定比例（分别为１％、２％、３％、４％、５