现代整体橱柜内微环境空气质量对健康的影响

本文用案例阐述了现代整体橱柜内微环境中的甲醛污染,导致了对人体健康的危害。并用体积相同而材料不同的橱柜进行柜内空气中甲醛的检测比对和柜内微环境中甲醛污染的调味品检测比对。     

西北5省(区)区域旅游经济差异变化——基于泰尔指数的测度

旅游经济的空间差异是区域经济发展不平衡的一种现象。利用旅游总收入和及其所占GDP的百分比2个测度指标,采用泰尔指数对1996--2005年西北5省（区）旅游经济差异变化进行了分析。结果发现,1996-2005年GDP权重的泰尔指数整体上处于下降趋势,而旅游总收入权重的泰尔指数处于微弱的上升趋势,不论何种指标权重由组内差距造成的差异在西北5省（区）旅游经济差异中处于主导地位。     

A_2型高粱细胞质雄性不育系与其保持系的胞质DNA和核DNA差异

以高粱细胞质雄性不育系A2 V4 (A)及其保持系V4 (B)的总DNA为模板 ,对 184个随机引物进行筛选 ,找到6个其RAPD扩增产物在A/B间存在稳定差异的引物 .将该 6个引物同时扩增A/B的总DNA、线粒体DNA(mtDNA)及叶绿体DNA(cpDNA) .以总DNA为模板时得到 12个扩增片段 ,以mtDNA为模板时得到 4个 ,以cpDNA为模板时得到 11个 .结果分析表明 ,在这些扩增片段中 ,有 7个仅仅出现在以胞质DNA为模板的扩增中 ,有 5个在以总DNA和胞质DNA为模板时同时出现 ,即认为这 12个片段来自胞质DNA .另有 7个片段 ,在以胞质DNA为模板时未出现 ,而是仅仅出现在以总DNA为模板的扩增中 ,认为是来自核DNA .来自核DNA的 7个扩增片段中 ,有 5个来自保持系 ,有 2个来自不育系 ,这表明 ,不育系与保持系在核DNA上存在差异 .对A/B核DNA在CMS中的重要性及研究对策进行了讨论 .图 2表 4参 19     

山东省潍坊市冰雹灾害发生规律及防灾措施

根据1991～1995年的气象观测资料,对滩坊市近期冰雹灾害发生规律进行了分析,同时提出了预防冰雹灾害的措施,着重指出了利用高炮和火箭防雹的科学性和可行性。     

西部开发中的泥石流问题

西部地区的青、甘、陕、川、滇、黔、新、藏、宇、桂、内蒙和重庆等12个省区市内都有泥石流分布,已查明的泥石流沟计15500余条,受泥石流危害或威胁的县级以上政府驻地城镇逾百座,一场泥石流致死百人以上的灾害点达23个,泥石流及其灾害是西部大开发中必须面临的生态环境问题之一,城市建设、公路和铁路等交通建设、水利建设,西气和西电东送工程建设等西部大开发的重点领域,,在开发建设中都将要遇到泥石流问题,吸取以往这类建设中抗御泥石流灾害的经验与教训,对于减轻泥石流灾害和保障西部大开发顺利进行具有现实意义。     

Metals in biomass

Background, Aim and Scope

Metal ions generally share the ability/tendency of interacting with biological material by forming complexes, except possibly for the heavy alkali metals K, Rb and Cs. This is unrelated to the metals being either essential for sustaining life and its reproduction, apparently insignificant for biology, although perhaps undergoing bioconcentration or even being outright toxic, even at low admission levels. Yet, those different kinds of metal-biomass interactions should in some way depend on properties describing coordination chemistries of these very metals. Nevertheless, both ubiquitously essential metals and others sometimes used in biology should share these properties in numeric terms, since it can be anticipated that they will be distinguished from nonessential and/or toxic ones. These features noted above include bioconcentration, the involvement of metal ions such as Zn, Mg, Cu, Fe, etc. in biocatalysis as crucial components of metalloenzymes and the introduction of a certain set of essential metals common to (almost) all living beings (K, Mg, Mo, Mn, Fe, Cu and Zn), which occurred probably very early in biological evolution by ‘natural selection of the chemical elements’ (more exactly speaking, of the metallomes).

Materials and Methods

The approach is semiempirical and consists of three consecutive steps: 1) derivation of a regression equation which links complex stability data of different complexes containing the same metal ion to electrochemical data pertinent to the (replaced) ligands, thus describing properties of metal ions in complexes, 2) a graphical representation of the properties-two typical numbers c and x for each metal ion-in some map across the c/x-space, which additionally contains information about biological functions of these metal ions, i.e. whether they are essential in general (e.g. Mg, Mn, Zn) or, for a few organisms of various kinds (e.g. Cd, V), not essential (e.g. rare earth element ions) or even generally highly toxic (Hg, U). It is hypothesized that, if coordination properties of metals control their biological ‘feasibility’ in some way, this should show up in the mappings (one each for mono and bidentate-bonding ligands). 3) eventually, the regression equation produced in step 1) is inverted to calculate complex stabilities pertinent to biological systems: 3a) complex stabilities are mapped for ligands delivered to soil (-water) by green plants (e.g. citrate, malate) and fungi and, compared to their unlike selectivities and demands of metal use (photosynthesis taking place or not), 3b) the evolution of the metallome during late chemical evolution is reconstructed.

Results

These maps show some ‘window of essentiality’, a small, contrived range/area of c and x parameters in which essential metal ions gather almost exclusively. c and x thus control the possibility of a metal ion becoming essential by their influencing details of metal-substrate or (in cases of catalytic activities) metal-product interactions. Exceptions are not known to be involved in biocatalysis anyhow.

Discussion

Effects of ligands secreted, e.g. from tree roots or agaric mycelia to the soil on the respective modes (selectivities) of metal bioconcentration can be calculated by the equation giving complex stability constants, with obvious ramifications for a thorough, systematic interpretation of biomonitoring data. Eventually, alterations of C, N and P-compounds during chemical evolution are investigated — which converted CH₄ or CO₂, N₂ and other non-ligands to amino acids, etc., for example, with the latter behaving as efficient chelating ligands: Did they cause metal ions to accumulate in what was going to become biological matter and was there a selectivity, a positive bias in favour of nowessential metals (see above) in this process? Though there was no complete selectivity of this kind, neither a RNA world in which early ribozymes effected most of biocatalysis, nor a paleoatmosphere containing substantial amounts of CO could have paved the way to the present biochemistry and metallomes.

Conclusions

This way of reasoning provides a causal account for abundance distributions described earlier in the Biological System of Elements (BSE; Markert 1994, Fränzle &; Markert 2000, 2002). There is a pronounced change from chemical evolution, where but few transformations depended on metal ion catalysis to biology.

Recommendations and Perspectives

The application of this numerical approach can be used for modified, weighted evaluation of biomonitoring analytical data, likewise for the prediction of bioconcentration hazards due to a manifold of metal ions, including organometallic ones. This is relevant in ecotoxicology and biomonitoring. In combining apoproteins or peptides synthesized from scratch for purposes of catalysing certain transformations, the map and numerical approaches might prove useful for the selection of central ions which are even more efficient than the ‘natural’ ones, like for Co²⁺ in many Zn enzymes.

     

Identification of Pollution Source of Cadmium in Soil. Application of Material Flow Analysis and A Case Study in Taiwan (11 pp)

Background Since the 1970s, at least 200 hectares (ha) of farmland has been polluted by the heavy metal cadmium (Cd).Consequently, the Cd pollution has led to contaminate the rice production and caused acute social panic. According to the recent investigation results performed by the Taiwan Environmental Protection Administration (TEPA), it is indicated that most of the Cd pollution incidents in Taiwan resulted from the wastewater discharge of stearate Cd factories. To prevent the Cd pollution incidents from spreading, the TEPA has either forced these factories to close down or assisted them in improving their production processes since the 1980s. Unfortunately, accidental incidents of Cd pollution still emerge in an endless stream, despite the strict governmental controls placed on these questionable factories. Whether this pollution has resulted from undetected or hidden pollution sources stemming from two decades ago or comes from some new source, will be an outstanding issue. Therefore, this study attempts to identify the pollution sources of Cd in soil in Taiwan as well as to find the solution to the above-mentioned, outstanding issue by way of a methodology termed Material Flow Analysis (MFA). Method logy. The MFA has proved to be a useful tool on providing quantitative information of the flow of substances through an economic to an environmental system. Based upon the supply-and-demand theory of MFA, researchers have successfully conducted an overview of the use of materials in many industries, the construction industry being one of these. Therefore, this study tries to establish a set of analytical processes by way of MFA for identifying the pollution source of Cd in soil in Taiwan. In addition, the spirit of Life Cycle Analysis (LCA) technique was also employed to identify the materials, and products should be ignored as a crucial pollution source in this study. Results and Discussion According to the MFA methodology applied in this study and on the basis of related studies performed by Taiwanese governmental authorities, we arrive at the following analysis results: (1) the total amount of Cd from the economic perspective of material and product flow was approximately 441.2 tons; (2) the wastewater directly discharged into irrigation water can be concluded to be the major pollution route of Cd in farmland soil in Taiwan; (3) material plastic stabilizer (cadmium oxide, CdO), Zn-Pd compounds and Cu compounds should be the crucial pollution sources to contaminate environment through the route of wastewater in Cd flow analysis; (4) the crucial pollution sources to contaminate environment through the route of wastewater in Cd flow analysis were five factories, Coin, Jili, Taiwan Dye, Guangzheng and Mingguan, and they were all categorized as stearate Cd industries; (5) the typical source of the Cd pollution in soil in Changhua County through the pollution route of wastewater should be the metal surfacing process industries. Conclusions This study proved that MFA can be a good tool for identifying Cd flow as well as for recognizing the crux of the problem concerning incidents of Cd pollution. This study led to the conclusion that the causal relationship between farmland pollution caused by Cd and stearate Cd factories in Taiwan seemed quite close by way of MFA methodology. In addition, this study also found that the wastewater discharged from a single metal surfacing process factory will not cause remarkable farmland pollution. However, the wastewater simultaneously discharged from a group of pollution factories can result in a significant pollution incident. Recommendations and Outlook This case study is only a small contribution to the understanding of the toxic material flow related to Cd in the environment. This study recommends that Taiwanese governmental authorities should not deal with problems on an ad hoc basis, but should instead deal with Cd pollution problems overall employing control measures. Finally, the more accurate information or data we can collect, the more reliable results we can identify. Therefore, the quality and quantity of related data used in this MFA model should be closely scrutinized in order to ensure the most correct and comprehensive investigation on the toxic material flow.     

Diel Cycling of Zinc in a Stream Impacted by Acid Rock Drainage: Initial Results from a New in situ Zn Analyzer

Recent work has demonstrated that many trace metals undergo dramatic diel (24-h) cycles in near neutral pH streams with metal concentrations reproducibly changing up to 500% during the diel period (Nimick et al., 2003). To examine diel zinc cycles in streams affected by acid rock drainage, we have developed a novel instrument, the Zn-DigiScan, to continuously monitor in situ zinc concentrations in near real-time. Initial results from a 3-day deployment at Fisher Creek, Montana have demonstrated the ability of the Zn-DigiScan to record diel Zn cycling at levels below 100 μg/l. Longer deployments of this instrument could be used to examine the effects of episodic events such as rainstorms and snowmelt pulses on zinc loading in streams affected by acid rock drainage.     

生态增益补偿问题探讨——对东西部生态补偿争议的思考

针对生态补偿增益层面理论研究相对薄弱及当前我国大规模生态工程建设中支付主体单一、资金不足的问题,本文分别从法学、经济学、东西部差异三个角度,通过理论与实例分析相结合的方式,论述了东部对西部实施生态补偿的必要性,提出了将区外受益政府和直接受益行业纳入补偿支付主体,生态增益层面不宜对全社会征收生态税,以及暂时不宜实行自我补偿的政策建议。     

用于高校优质中水原位处理的设备研究

为了提高高校优质中水的处理与回用率,提出了适用于高校优质中水的处理与回用系统,设计了中水原位处理设备,并进行了试验验证.结果表明,沉淀-SOBMR-过滤设备能够实现无动力、自动化运行,尤其适合于盥洗和洗浴废水的处理.沉淀单元对盥洗废水COD和SS去除率分别为23.8%和55.7%;SOBMR单元对盥洗废水COD和SS去除率分别为35.8%和27.9%;过滤单元能有效去除废水中绝大部分SS,且能耐受SS冲击负荷,对废水COD去除率先增后降,受水力负荷的影响,负荷越小,处理效果越好.整个系统出水水质满足杂用水对COD、SS和色度等要求,可用于冲厕和杂用.每套处理装置可节约水资源151.2 m3/a,设备投资回收期为2.01年,具有巨大的经济效益.