中日韩循环经济政策比较研究

在中国经济迅猛发展的同时，投资主导型的经济模式中环境保护要素的缺失导致我国工业化发展旱、中期的资源、能源约束、效率低下和浪费严重。在我国实施循环经济刻不容缓。循环经济政策是依据不同的社会、经济和环境条件而制定的。由于历史的原因，中日韩三国在地缘关系、政治传统、风俗习惯、文化教育等内在制度和外在制度彼此趋同，反映在循环经济政策的制定、执行上也有某些相似的地方。对三国循环经济的历史和现状进行比较研究，得出有益于我国的经验，无疑具有很重大的现实意义。采用制度变迁的基本理论作为指导，运用历史研究法、调查研究法等方法进行研究，对中日韩循环经济政策演变的历程进行系统梳理和比较，深入全面地考量其指导思想和举措的选择动机，系统广泛地从多方面研究中日韩循环经济政策。并将三者加以比较，以得出对我国循环经济的发展具有较强借鉴意义的经验，更好地推进循环经济在我国的发展。     

中国工业污染防治的战略决策——清洁生产

本文简述了清洁生产的概念与国外清洁生产的概况，评述了国内工业生产的现状及推行清洁生产的潜力和前景，并提出了一些有益建议。     

江苏省第三产业清洁生产方案的研究

本文通过对第三产业中宾馆饭店、旅游园林、学校等试点单位开展清洁生产的具体措施 ,分析第三产业清洁生产的特点 ,建立第三产业清洁生产的标准规范 ,提出可操作的第三产业实施清洁生产的程序方案 ,探索第三产业发展与环境保护和谐统一的途径     

旅游业推行清洁生产与可持续旅游发展

本文尝试将清洁生产的理论与方法导入旅游业 ,探讨了旅游业清洁生产的概念、必要性、内容和模式 ,进而就旅游业清洁生产与可持续旅游发展的关系及清洁生产的实施途径进行了探讨     

NITROGEN TRANSFORMATIONS IN SEDIMENTS AS AFFECTED BY CHEMICAL AMENDMENTS1

ABSTRACT: A study was conducted to elucidate some of the chemical factors affecting the rate and pathways of N transformations in lake sediments. The main emphasis was placed on modifying a noncalcareous sediment with CaCO₃ to approximate the composition of a calcareous sediment. Additionally, the effects of Ca²⁺, CO₃^2-, Mg2⁺ and OH^- were evaluated by using appropriate chemicals. Further, the effect of aluminum sulfate was evaluated with both sediment types. Sediment pH at 7 days was not affected by CaCO₃, but was decreased by aluminum sulfate. The CaCO₃ treatment increased the rate of ammonification, nitrification, reduction of acetylene to ethylene and methane formation, while with few exceptions the other treatments decreased the rate of the transformations studied. Aluminum sulfate, which has been proposed as a lake restoration treatment, increased ammonification but decreased most of the other transformations.     

The Loch Fleet Project in the Context of Acidification Reduction Measures

At Loch Fleet, and in other liming studies in similar environments, catchment liming is successful if an adequate amount of lime is added to hydrological source areas. Geochemical modelling demonstrates that the relatively late acidification of L. Fleet is consistent with the ameliorating effect of an alkaline groundwater input: the presence of this input implies that had the Loch not been limed in 1985 it would have recovered to conditions suitable for fish in about 20 years, given current commitments to sulphur emission reductions. Lakes without similar alkaline groundwater are not likely to recover as quickly. the different consequences of liming and emission reduction as methods of restoring acid waters are reviewed and contrasted. Restoration of waters by liming may result in some undesirable effects on the terrestrial catchment: these are discussed but it is concluded that catchment liming, used with discrimination, can be an acceptable management tool.     

矿山清洁生产示范研究

矿山清洁生产具有双重性。矿山生命周期决定了矿山清洁生产体系的特殊性。矿山清洁生产体系是由培训体系、生命周期清洁生产体系和监合与审核体系构成的一个系统，生命周期清洁生产体系包括从资源勘探-规划设计-开发-闭矿-后续土地利用与监测的各个阶段。与其他行业相比，矿山清洁生产难度大且明显滞后，开展矿山清洁生产示范研究势在必行。     

腐殖酸对砂质土壤吸附Cr(VI)的影响

利用系列摇瓶振荡实验,研究了在砂质土壤介质中腐殖酸(HA)对Cr(VI)还原作用及增强土壤表面对其吸附的影响.通过改变反应接触时间、pH值、HA投加量等条件,确定了最佳吸附反应条件.结果表明:砂质土壤中存在HA时,可使Cr(VI)还原为毒性较小的Cr(Ⅲ),明显增强土壤对可溶态Cr离子的吸附能力,比同等条件下无HA的土壤吸附量增大1倍以上.一般整个反应过程约8 h即可达到稳定.pH值对Cr的还原和吸附有很大的影响,酸性条件下的吸附量比碱性条件可增大1倍,最佳pH值为2～4;当pH＞5时吸附能力急剧下降,pH=10时吸附去除量降为20%.有HA存在时砂质土壤土对Cr(VI)的吸附反应为一级动力学反应,K298=0.033 5 min-1,砂土对CrO2-4的等温吸附曲线较好地满足Langmuir公式.     

In-situ electrochemical measurements of total concentration and speciation of heavy metals in acid mine drainage (AMD): assessment of the use of anodic stripping voltammetry

We assessed the use of anodic stripping voltammetry (ASV) for in-situ determinations of both total concentration and speciation of dissolved heavy metals (Cd, Cu, Pb and Zn) in acid mine drainage (AMD). In the Kwangyang Au–Ag mine area of South Korea, different sites with varying water chemistry within an AMD were studied with a field portable anodic stripping voltammeter. Anodic stripping voltammetry after wet oxidation (acidification) was very sensitive enough to determine total concentration of dissolved Cd because Cd was dominantly present as ‘labile’ species, whilst the technique was not so effective for determining total Cu especially in the downstream sites from the retention pond, due to its complexation with organic matter. For dissolved Pb, the concentrations determined by ASV after wet oxidation generally agreed with those by ICP-AES. In the downstream samples (pH>5), however, ASV data after wet oxidation were lower than ICP-AES data because a significant fraction of dissolved Pb was present in those samples as ‘inert’ species associated with colloidal iron oxide particles. The determination of total dissolved Zn by ASV after wet oxidation appeared to be unsatisfactory for the samples with high Cu content, possibly due to the interference by the formation of Zn–Cu intermetallic compounds on the mercury coated electrode. In AMD samples with high dissolved iron, use of ultraviolet irradiation was not effective for determining total concentrations because humate destruction by UV irradiation possibly resulted in the removal of a part of dissolved heavy metals from waters through the precipitation of iron hydroxides.     

Effect of natural organic matter on arsenic release from soils and sediments into groundwater

Arsenic (As) contamination in groundwater has received significant attention recently. Natural and anthropogenic sources contribute to the worldwide occurrence of As contamination. As speciation is an important factor related to its toxic and mobile behavior. The release of As from soils and sediments into groundwater is governed by several geophysicochemical processes, of which, As sorption behavior is of principle significance. This review paper summarizes existing information regarding the effects of natural organic matter (NOM) on the fate and mobility of As species in the environment. NOM may enhance the release of As from soils and sediments into the soil solution, thereby facilitating As leaching into the groundwater. The main influencing mechanisms include competition for available adsorption sites, formation of aqueous complexes, and/or changes in the redox potential of site surfaces and As redox speciation. NOM may also serve as binding agents, thereby reducing As mobility. However, comparably little research has been performed on this aspect. Since most investigations have been done on purified minerals under laboratory conditions, further research involving various geological materials under natural environmental conditions is required. Development of proper geochemical conceptual models may provide means of predicting the role of NOM in arsenic leaching and/or immobilization.