Carbon emissions from the peat fire problem—a review

Environmental Science and Pollution Research - Peat fires in tropical peatland release a substantial amount of carbon into the environment and cause significant harm to peatlands and the ecology,...     

电厂输煤系统电除尘设备防燃防爆设计及处理措施的探讨

文章针对电厂输煤系统的除尘选择配置电除尘器时出现的燃爆事故,尝试从设备和系统的防燃爆设计原理进行分析,提出设备和系统的设计原则和运行中的防燃防爆措施。     

Fenton试剂催化氧化法处理离子交换树脂再生废水

针对离子交换树脂再生废水中的难降解有机物利用Fenton试剂进行催化氧化处理。实验结果表明：当反应条件是H2O2与FeSO4·7H2O摩尔比为5：1、H：O2（30％）投加量为0．35mol／L（4次投加）、pH值为3．5、反应时间为2h时,废水的处理效果最佳;并采用正交实验确定了各反应因素对废水的CODcr去除效果的影响水平。     

不同淋洗剂对镍污染砂土的柱淋洗研究

比较了去离子水、阴离子表面活性剂十二烷基硫酸钠（SDS）、盐酸和柠檬酸对模拟污染砂土中镍（Ⅱ）的柱淋洗作用。SDS浓度为500、1000、1750、2500和3250mg／L,盐酸溶液pH值为0．8、1、2和3,柠檬酸溶液浓度为0．01、0．04、0．1和0．4mol／L。结果表明,几种淋洗剂对土柱中镍的淋洗曲线规律相似,即在淋洗液孔隙体积数为0．5时开始有镍淋出,随着累计孔体积数目的增大,淋洗液中镍的浓度逐渐开始增大,迭到峰值时又开始减小。在去离子水淋洗过程中,镍最大淋出浓度为90．8mg/L;五种不同浓度SDS淋洗过程中,镍最大淋出浓度分别为92．4、90．2、94．1、51．0和53．7mg／L;四种不同pH值的盐酸溶液对应的镍最大淋出浓度分别为959．5、753．3、56．3和23．9mg／L;四种不同浓度的柠檬酸对应的镍最大淋出浓度分别为318．6、793．4、930．1和1464．4mg／L。pH=1的盐酸溶液对镍的淋洗去除率最高为87．3％,其次是浓度为0．1mol／L的柠檬酸溶液,去除率为83．2％;SDS的淋洗效率低,与去离子水相当。0．1mol／L的柠檬酸溶液可为污染土壤重金属镍淋洗用试剂。     

应急管理中的动态车辆调度

近年来,应急管理引起了人们的重视,相关的研究也不断深入,在应急管理研究中运筹学发挥的作用日见显著,本文用运筹学中的规划方法给出了解决在“完成时间最早且总运行时间最少“约束下的应急车辆动态调度的模型,并给出了算法,最后通过案例分析了模型和算法的求解过程,提出了最优的调度方案,说明了方法的可行性.     

End-of-life vehicle recycling and international cooperation between Japan,China and Korea: Present and future scenario analysis

In the area of end-of-life vehicle (ELV) recycling, Japan passed the Automobile Recycling Law in January 2005, the first in Asia. Korea followed suit with the passage of the resource circulation method in 2009. China is expected make a new recycling law in 2011. In contribution to these initiatives, Tohoku University made a comparative analysis of ELV recycling laws, advance dismantling experiments and scenario analysis to promote international cooperation. This is envisioned to introduce ELV recycling system in Japan, China and Korea and in developing countries as well.     

用马尔可夫链模型预测宁南山区旱情

宁南山区干旱频繁,严重影响农业生产。根据固原气象站35年(1957～1991)雨量资料,应用马尔可失链模型预测了该区1992～1996年的雨量与旱情趋势。结果表明,今后五年将出现三年春夏旱、二年正常,秋季有四年正常、一年多雨;预测的1992年4～6月和6～9月的干旱等级值与实际完全相符。该模型预测结果有较高可信度,对该区农业生产有参考价值。     

油污土壤的生物处理技术及其影响因素分析

生物处理技术可以用于转化和去除土壤中的石油类污染物,微生物对油污土壤产生降解作用,其降解的最终产物是CO2和水,不产生二次污染。重点分析了影响微生物降解的主要因素,包括pH值、温度、湿度、供氧情况、营养素、表面活性剂加入量、油污染强度,论述了各种影响因素的调整和控制方法。     

Activities of Po and Pb in the water column at Kuala Selangor, Malaysia

Natural radionuclides, such as ²¹⁰Po and ²¹⁰Pb were measured in the water samples collected from six stations at Kuala Selangor, Malaysia. Results for ²¹⁰Po and ²¹⁰Pb in dissolved and particulate phases have showed the difference in distribution and chemical behavior. The fluctuation activities of ²¹⁰Po and ²¹⁰Pb depend on wave action, geology and degree of fresh water input occurring at study areas and probably due to different sampling dates. The distribution coefficient, K_d, values of ²¹⁰Po and ²¹⁰Pb ranged from 2.0 × 10³ l g⁻¹ to 265.15 × 10⁵ l g⁻¹, and from 3.0 × 10³ l g⁻¹ to 558.16 × 10⁵ l g⁻¹, respectively. High K_d values of ²¹⁰Po and ²¹⁰Pb indicated that a strong adsorption of ²¹⁰Po and ²¹⁰Pb onto suspended particles, and the sinking of both nuclides on the seabed at study locations were controlled by the characteristics of suspended particles.     

Selective redox degradation of chlorinated aliphatic compounds by Fenton reaction in pyrite suspension

Selective redox degradation of chlorinated aliphatics by Fenton reaction in pyrite suspension was investigated in a closed system. Carbon tetrachloride (CT) was used as a representative target of perchlorinated alkanes and trichloroethylene (TCE) was used as one of highly chlorinated alkenes. Degradation of CT in Fenton reaction was significantly enhanced by pyrite used as an iron source instead of soluble Fe. Pyrite Fenton showed 93% of CT removal in 140 min, while Fenton reaction with soluble Fe(II) showed 52% and that with Fe(III) 15%. Addition of 2-propanol to the pyrite Fenton system significantly inhibited degradation of TCE (99% to 44% of TCE removal), while degradation of CT was slightly improved by the 2-propanol addition (80-91% of CT removal). The result suggests that, unlike oxidative degradation of TCE by hydroxyl radical in pyrite Fenton system, an oxidation by the hydroxyl radical is not a main degradation mechanism for the degradation of CT in pyrite Fenton system but a reductive dechlorination by superoxide can rather be the one for the CT degradation. The degradation kinetics of CT in the pyrite Fenton system was decelerated (0.13-0.03 min⁻¹), as initial suspension pH decreased from 3 to 2. The formation of superoxide during the CT degradation in the pyrite Fenton system was observed by electron spin resonance spectroscopy. The formation at initial pH 3 was greater than that at initial pH 2, which supported that superoxide was a main reductant for degradation of CT in the pyrite Fenton system.