农村面源污染治理建议与对策

文章对农村面源污染进行了简要介绍，综述了抚顺县农村面源污染现状、存在的主要问题及产生的原因。并对如何缓解目前农村面源污染提出了合理化建议与对策。     

扬子鳄资源数量、价值及开发利用现状

对扬子鳄资源的经济、生态及科研价值进行合理的评价；根据扬子鳄野外及人工养殖的资源数量,论述了扬子鳄资源开发利用的现状及存在的问题,并分析了扬子鳄资源开发利用的发展对策     

环境污染系统的灰色投入产出模型

将投入产出模型与灰色理论结合起来，建立了以灰色预测为基础的环境污染系统灰色投入产出模型，探索了如何从污染物总量控制目标出发来规划和发展生产。     

有机磷农药敏化作用的初步研究

本文研究了有机磷农药甲基1605和毒死蜱对~1O_2探针性物质二乙基二硫酸(DES)、萜品烯(α-terp)及ROO和RO探针性物质2.6-二叔醒基-4-甲基苯酚(BHT)和1,2,3,4-四氢萘(tetra)光降解的敏化作用.结果表明基态氧直接参与了DES和α-terp的光解;在甲基1605的作用下,1/K_(exptl)与[α-terp]的关系表明,α-terp的降解不为~1O_2历程;同时BHT和tetra的敏化降解说明ROO的量子产率为~1O_2量子产率的5倍;对氯氰菊酯的光敏降解产物的检测表明,在甲基1605存在下,产物仍然以~3O_2氧化产物为主.     

电气石在环境领域的最新应用研究：处理雅格素蓝BF-BR染料废水

在氧化剂(H2O2)的协同作用下,电气石对雅格素蓝BF-BR染料废水具有良好的脱色能力,脱色率与电气石用量、氧化剂用量、水浴温度、作用时间呈正相关性,溶液pH值为2和12时,脱色率最大.正交实验优化了工艺条件:氧化剂用量1.5 mL、作用时间9 min、电气石用量1g、水浴温度363 K、pH=2,此时脱色率可达到100%.动力学研究表明:雅格素蓝BF-BR染料废水的脱色反应为一级反应,其反应表观动力学方程为:-lnCR=0.36733t-lnC0(R=0.9827),反应速率常数为k=0.36733 min-1,反应半衰期为t1/2=1.887 min.机理的初步分析表明:脱色过程是矿物催化-类芬顿反应.     

煤矸石微生物脱硫试验研究

采用本试验室自主分离筛选出的氧化硫硫杆菌,通过煤矸石浸泡的微生物脱硫和煤矸石柱状淋洗的微生物脱硫试验,研究该菌株对大武口高硫煤矸石的脱硫效果.煤矸石浸泡试验表明,微生物对煤矸石脱硫效果明显,浸泡煤矸石2 h后脱硫量达0.79 g/L,脱硫率达24.5%,21 d持续稳定升高,脱硫率达28.3%,为煤矸石的快速脱硫提供了技术支持.煤矸石柱状淋洗试验表明,前9 d是氧化硫硫杆菌脱硫的活跃期,该菌株有较高的氧化煤矸石的能力.     

考虑源头减量的城市生活垃圾管理系统动力学研究

文章根据计划行为理论,使用系统动力学的方法,设计了考虑源头减量的城市生活垃圾管理的系统动力学模型.该模型动态地仿真了管理系统中宏观和微观的因素之间随时间推移的相互作用.通过分析管理模型中各个子模型的仿真结果,说明了源头减量对垃圾管理的重要意义.     

模拟酸雨对菜豆叶片的伤害和Mefluidide保护效应的研究

酸雨的污染和危害已成为一个世界性的问题,我国的酸雨危害也日渐引起关注.由于酸雨所涉及到的地区不少是农作区,必然会危及农作物的产量.近年来对酸雨危害作物的机理已有报道,但关于寻求保护作物免于酸雨危害的研究则不多见.已有报道,Mefluidide(N-[2,4-dimethyl-5-[(trifluoromethyl)sulfonyl]amino]phenylacetamide)(N-[2,4-二甲基-5-[(三氟甲基)磺酰]氨基]苯乙酰胺),一种合成的植物生长调节物质,对植物生长和发育以及物质代谢都有影响,尤其是能有效地保护低温敏感作物免于冷害,而且发现Mefluidide处理的植物,在冷害期间不表现细胞膜透性的增加.另外,有人发现pH2.0—4.0的模拟酸雨喷洒植株(青菜、菠菜和萝卜等)也会导致膜透性增加.我们以模拟酸雨引起菜豆叶片的伤害症状和一些生理指标为依据,     

Wireless charging and shared autonomous battery electric vehicles (W+SABEV): synergies that accelerate sustainable mobility and greenhouse gas emission reduction

Mitigation and Adaptation Strategies for Global Change - Emerging technologies play important roles in shaping future mobility systems and impacting sustainability performance of the transportation...     

Simultaneous Fe(III) reduction and ammonia oxidation process in Anammox sludge

In recent years, there have been a number of reports on the phenomenon in which ferric iron (Fe(III)) is reduced to ferrous iron [Fe(II)] in anaerobic environments, accompanied by simultaneous oxidation of ammonia to NO₂^-, NO₃^-, or N₂. However, studies on the relevant reaction characteristics and mechanisms are rare. Recently, in research on the effect of Fe(III) on the activity of Anammox sludge, excess ammonia oxidization has also been found. Hence, in the present study, Fe(III) was used to serve as the electron acceptor instead of NO₂^-, and the feasibility and characteristics of Anammox coupled to Fe(III) reduction (termed Feammox) were investigated. After 160days of cultivation, the conversion rate of ammonia in the reactor was above 80%, accompanied by the production of a large amount of NO₃^- and a small amount of NO₂^-. The total nitrogen removal rate was up to 71.8%. Furthermore, quantities of Fe(II) were detected in the sludge fluorescence in situ hybridization (FISH) and denaturated gradient gel electrophoresis (DGGE) analyses further revealed that in the sludge, some Anammox bacteria were retained, and some microbes were enriched during the acclimatization process. We thus deduced that in Anammox sludge, Fe(III) reduction takes place together with ammonia oxidation to NO₂^- and NO₃^- along with the Anammox process.