ISOLATION AND SEPARATION OF TALL FESCUE AND RYEGRASS ALKALOIDS’

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火试金富集-重量法测定冰铜中金

火试金富集-重量法测定冰铜中金

火试金富集-重量法测定冰铜中金何炼;肖刚【摘要】The direct determination of gold content in matte by fire assaying was studied. The optimal experiment conditions were obtained. When the added amount of lead oxide was 35 times of copper, the added amount of sodium borate was 15 g, the ratio of solvent sample and Na2CO3 was 1 : 0. 7, the melting temperature was 1 100 ℃ , the constant temperature was 1 200 ℃ , and the constant temperature time was 30 min, the sample enrichment, separation and prepared lead button by melting were best. Five actual matte samples were analyzed. The results were compared with those obtained by atomic absorption spectrometry. It was found that, the analysis results of gold content in matte by this method were consistent with those obtained by atomic absorption spectrometry. The recoveries of standard addition were 90%-107%. The relative standard deviation (RSD) was 2. 4 %-4. 9 %.%研究了采用火试金法直接测定冰铜中的金的含量,确定了最佳实验条件.在氧化铅加入量达到铜量的35倍、硼砂加入量为15 g、溶剂样品与Na2 CO3比为1∶0.7的条件下,且熔融温度为1 100℃、恒温温度为1 200℃、恒温时间为30 min时样品富集分离熔融制备的铅扣效果最好.分析了5个冰铜实际样品,并与原子吸收光谱法进行对比,研究结果表明:方法分析冰铜中的金含量时,分析结果与原子吸收光谱法分析值相吻合,加标回收率为90%~107%.方法的相对标准偏差为2.4%~4.9%.【期刊名称】《冶金分析》【年(卷),期】2013(033)003【总页数】4页(P69-72)【关键词】火试金法;铅扣;冰铜;金;重量法【作者】何炼;肖刚【作者单位】中国地调局沈阳地质调查中心,辽宁沈阳110032【正文语种】中文【中图分类】O655.1冰铜是指重金属火法熔炼过程中产出的重金属硫化物的共融体,是以Cu2 S-FeS系为主要成分并少量溶解其他金属硫化物(如PbS、ZnS、Ni3 S2等)、氧化铁、贵金属及微量脉石成分的多元系混合体[1-2]。

湿法炼锌中锌铁分离方法与运用探讨

湿法炼锌中锌铁分离方法与运用探讨

・20・有色金属(冶炼部分)(http://)2021年第2期doi:10.3969/j.issn.1007-7545.2021.02.003湿法炼锌中锌铁分离方法与运用探讨张国华,朱北平,陈先友,姚应雄,成世雄,李云,李科(云锡文山锌锢冶炼有限公司,云南文山663701)摘要:湿法炼锌已成为锌冶炼的主流趋势.铁闪铮矿作为当今锌冶炼的主要原料•铁的分离成为其在湿法炼锌过程中的关键环节,湿法炼锌工艺流程的选择很大程度上就是锌铁分离方法的选择。

阐述了铁闪锌矿在湿法炼锌过程中几种主要的锌铁分离方法及其工艺原理、工艺控制条件、主要经济技术指标,并且分析了工艺的优缺点•为湿法炼锌企业锌铁分离方法的选择和运用提供依据。

关键词:挥发法;黄钾铁矶法;针铁矿法;赤铁矿法;铁资源化中图分类号:TF813文献标志码:A文章编号:1007-7545(2021)02-0020-07Discussion on Separation Method and Application of Zinc andIron in Zinc HydrometallurgyZHANG Guo-hua,ZHU Bei-ping,CHEN Xian-you.YAC)Ying-xiong,CHENG Shi xiong,LI Yun,LI Ke(Yunxi Wenshan Zinc Indium Smelting Co..Ltd..Wcnshan663701,Yunnan,China)Abstract:Zinc hydrometallurgy has become the mainstream trend of zinc smelting.Sphalerite is main raw material of zinc smelting,iron separation has become a key link in zinc hydrometalluegy.Choice of zinc smelting process is largely choice of zinc-iron separation method.Several main zinc-iron separation methods and process principles,process control conditions,and main economic and technical indicators of zinc hydrometallurgy process of sphalerite were described.Advantages and disadvantages of those processes were analyzed which can provide reference of selection and application of zinc-iron separation methods. Key words:volatilization method;jarosite method;goethite method;hematite method;iron resource utilization随着高锌低铁锌资源的不断开发利用,高品质锌资源逐渐减少,高铁复杂锌精矿成为当前锌冶炼的主要原料,同时也势必带来更多的杂质分离问题•包括铁的分离。

专业英语lesson14

专业英语lesson14

Lesson 14Air pollutionAir pollution is the human introduction into the atmosphere of chemicals, particulate matter, or biological materials that cause harm or discomfort to humans or other living organisms, or damages the natural environment. Air pollution causes deaths and respiratory disease. Air pollution is often identified with major stationary sources, but the greatest source of emissions is mobile sources, mainly automobiles. Gases such as carbon dioxide, which contribute to global warming, have recently gained recognition as pollutants by climate scientists, while they also recognize that carbon dioxide is essential for plant life through photosynthesis.The atmosphere is a complex,dynamic natural gaseous system that is essential to support life on planet Earth. Stratospheric ozone depletion due to air pollution has long been recognized as a threat to human health as well as to the Earth's ecosystems.An air pollutant is known as a substance in the air that can cause harm to humans and the environment. Pollutants can be in the form of solid particles, liquid droplets, or gases. In addition, they may be natural or man-made.Pollutants can be classified as primary or secondary. Usually, primary pollutants are directly emitted from a process, such as ash from a volcanic eruption, the carbon monoxide gas from a motor vehicle exhaust or sulfur dioxide released from factories.Secondary pollutants are not emitted directly. Rather, they form in the air when primary pollutants react or interact. An important example of a secondary pollutant is ground level ozone —one of the many secondary pollutants that make up photochemical smog.Note that some pollutants may be both primary and secondary: that is, they are both emitted directly and formed from other primary pollutants.Major primary pollutants produced by human activity include:●Sulfur oxides (SOx) especially sulfur dioxide, a chemical compoundwith the formula SO2. SO2 is produced by volcanoes and in various industrial processes. Since coal and petroleum often contain sulfur compounds, their combustion generates sulfur dioxide.Further oxidation of SO2, usually in the presence of a catalyst such as NO2, forms H2SO4, and thus acid rain. This is one of the causes for concern over the environmental impact of the use of these fuels as power sources.●Nitrogen oxides (NOx) especially nitrogen dioxide are emitted fromhigh temperature combustion. Can be seen as the brown haze dome above or plume downwind of cities. Nitrogen dioxide is the chemical compound with the formula NO2. It is one of the several nitrogen oxides. This reddish-brown toxic gas has a characteristic sharp, biting odor. NO2 is one of the most prominent air pollutants.●Carbon monoxide - is a colorless, odorless, non-irritating butvery poisonous gas. It is a product by incomplete combustion of fuel such as natural gas, coal or wood. Vehicular exhaust is a major source of carbon monoxide.●Carbon dioxide (CO2),a greenhouse gas emitted form combustion.●Volatile organic compounds VOCs are an important outdoor airpollutant. In this field they are often divided into the separate categories of methane (CH4) and non-methane (NMVOCs). Methane is an extremely efficient greenhouse gas which contributes to enhanced global warming. Other hydrocarbon VOCs are also significant greenhouse gases via their role in creating ozone and in prolonging the life of methane in the atmosphere, although the effect varies depending on local air quality. Within the NMVOCs, the aromatic compounds benzene, toluene and xylene are suspected carcinogens and may lead to leukemia through prolonged exposure.1,3-butadiene is another dangerous compound which is often associated with industrial uses.●Particulate matter Particulates, alternatively referred to asparticulate matter (PM) or fine particles, are tiny particles of solid or liquid suspended in a gas. In contrast, aerosol refers to particles and the gas together. Sources of particulate matter can be man made or natural. Some particulates occur naturally, originating from volcanoes, dust storms, forest and grassland fires, living vegetation, and sea spray. Human activities, such as the burning of fossil fuels in vehicles, power plants and various industrial processes also generate significant amounts of aerosols. Averaged over the globe, anthropogenic aerosols—those made by human activities—currently account for about 10 percent of the total amount of aerosols in our atmosphere. Increased levels of fine particles in the air are linked to health hazards such as heart disease, altered lung function and lung cancer.●Toxic metals, such as lead, cadmium and copper.●Chlorofluorocarbons (CFCs), harmful to the ozone layer emittedfrom products currently banned from use.●Ammonia (NH3),emitted from agricultural processes. Ammonia is acompound with the formula NH3. It is normally encountered as a gas with a characteristic pungent odor. Ammonia contributes significantly to the nutritional needs of terrestrial organisms by serving as a precursor to foodstuffs and fertilizers. Ammonia,either directly or indirectly, is also a building block for the synthesis of many pharmaceuticals. Although in wide use, ammonia is both caustic and hazardous.●Odors,such as from garbage, sewage, and industrial processes.● Radioactive pollutants produced by nuclear explosions, warexplosives, and natural processes such as the radioactive decay of radon.Secondary pollutants include:●Particulate matter formed from gaseous primary pollutants andcompounds in photochemical smog. Smog is a kind of air pollution;the word “smog” is a portmanteau of smoke and fog. Classic smog results from large amounts of coal burning in an area caused bya mixture of smoke and sulfur dioxide. Modern smog does not usuallycome from coal but from vehicular and industrial emissions that are acted on in the atmosphere by sunlight to form secondary pollutants that also combine with the primary emissions to form photochemical smog.●Ground level ozone (O3) formed from NOx and VOCs. Ozone (O3) isa key constituent of the troposphere (it is also an importantconstituent of certain regions of the stratosphere commonly known as the Ozone layer). Photochemical and chemical reactions involving it drive many of the chemical processes that occur in the atmosphere by day and by night. At abnormally high concentrations brought about by human activities (largely the combustion of fossil fuel), it is a pollutant, and a constituent of smog.●Peroxyacetyl nitrate (PAN) - similarly formed from NOx and VOCs.Minor air pollutants include:● A large number of minor hazardous air pollutants. Some of theseare regulated in USA under the Clean Air Act and in Europe under the Air Framework Directive.● A variety of persistent organic pollutants, which can attach toparticulate matter.Persistent organic pollutants (POPs) are organic compounds that are resistant to environmental degradation through chemical, biological, and photolytic processes. Because of this, they have been observed to persist in the environment, to be capable of long-range transport, bioaccumulate in human and animal tissue, biomagnify in food chains, and to have potential significant impacts on human health and the environment.14课:空气污染空气污染是人类引入氛围的化学品、颗粒、或生物材料,造成损害或不舒服,人类或其他生物破坏的自然环境。

Guidelines for ecological compensation associated with highways

Guidelines for ecological compensation associated with highways

Guidelines for ecological compensation associated with highwaysRuud Cuperus a,*,Kees J.Canters b ,Helias A.Udo de Haes b ,Debra S.Friedman caMinistry of Transport,Public Works and Water Management,Directorate-General of Public Works and Water Management,Road and Hydraulic Engineering Division,PO Box 5044,2600GA Delft,The Netherlands bCentre of Environmental Science,Leiden University,PO Box 9518,2300RA Leiden,The Netherlandsc265Gateway Drive,#210,Paci®ca,CA 94044,USAReceived 13February 1998;received in revised form 18November 1998;accepted 8December 1998AbstractAvoidance,mitigation and compensation are three planning concepts designed to counteract the adverse impacts of infra-structure on nature.To promote the compensation principle introduced in the Netherlands,this article proposes guidelines for its implementation in the context of highway development.To this end,a coherent framework has been developed comprising:(1)impacts on nature,(2)concepts for use in planning ecological compensation,and (3)ecological,spatial-planning and ®nancial instruments for realizing such compensation.Finally,the Dutch experience is discussed within the international context.Recom-mendations are made for improving the implementation of compensation.These stress the importance of creating `win±win'situa-tions to increase public support,of dealing with impacts that cannot be predicted,and of developing criteria for evaluating compensation plans.There are still several priority problems to be dealt with:the e ects of habitat isolation caused by highway projects,the e ectiveness of compensation measures and compensation ratios (viz.ratios of replacement to lost area)greater than one,the real costs associated with replacing habitats,the feasibility of compensation for ecological values that are di cult to replace,and the strategy to exchange impacted and substitute habitats.#1999Elsevier Science Ltd.All rights reserved.Keywords:Policy;Planning;Realization;Legislation;Instruments;Costs1.IntroductionThe construction and use of highways imply the loss,degradation and fragmentation of habitats (Andrews,1990;Bennett,1991;Atkinson and Cairns,1992;For-man and Hersperger,1996;Canters,1997).Increased awareness of environmental problems caused by infra-structure has moved civil engineers,ecologists and pol-icy-makers to develop planning concepts to deal with the impacts on nature and landscape,as embodied,for example,in the US National Environmental Policy Act (NEPA)regulations (1969).The ®rst,and most funda-mental approach is to avoid adverse impacts.Avoid-ance can be achieved by simply not pursuing a certain development,by generating an alternative for the development or by limiting the intensity or magnitude of the development.If avoidance is not feasible,mitiga-tion measures can be undertaken as a second planning concept.Such measures are designed to reduce orsometimes even eliminate the impacts of a given devel-opment on nature.Today,it is common practice worldwide to back up highway projects with mitigation measures,such as ecological management of roadside verges (Way,1977),fauna tunnels (Hunt et al.,1987;Bekker and Canters,1997),adapted culverts (Yanes et al.,1995)and ecoducts (P®ster and Keller,1995;Fried-man,1997)for wildlife movements.Recently,a third concept has been developed.Based on the experience that impacts may still persist after mitigation,several states and countries have adopted a compensation principle,envisaged as counterbalancing the adverse impacts of developments on nature.Exam-ples of such a principle are:the German Ein-gri sregelung (functioning since 1976;cf.Meier,1987),the US no-net-loss policy for wetlands (since 1986;cf.Section 404of the Clean Water Act),and the Dutch compensation principle for spatial protected areas (since 1993;cf.MANF and MHPE,1993).This concept explicitly incorporates nature conservation interests in decision-making on spatial developments.The initial consequences of the compensation principle for Dutch highways have been discussed by Van Bohemen (1995).0006-3207/99/$-see front matter #1999Elsevier Science Ltd.All rights reserved.P I I:S 0006-3207(99)00007-5Biological Conservation 90(1999)41±51*Corresponding author.Tel.:+31152518341;e-mail:r.cuper-us@dww.rws.minvenw.nlHowever,the principle has raised urgent questions about the basis for its implementation.This article proposes guidelines for implementing the compensation principle in the context of highway development.After de®ning the setting of ecological compensation(Section2),the impacts of highways on nature(3)are brie¯y described.Subsequently,concepts for use in planning ecological compensation measures (4)and instruments for their practical realization(5)are presented.The article concludes with a discussion of the evolving Dutch experience in the international context and identi®es problems that are still to be solved(6).2.The setting of ecological compensation Ecological compensation is de®ned here as the sub-stitution of ecological functions or qualities that are impaired by(highway)development(Cuperus et al., 1996).Such compensation aims either to improve damaged areas or to create new habitat with ecological functions and quality attributes(Allen and Feddema, 1996).Fundamentally,this does not di er from ecolo-gical restoration or habitat creation(Anderson,1995; Wyant et al.,1995),except that it is associated with adverse impacts on nature due to development.More-over,in contrast to mitigation measures,ecological compensation is generally undertaken outside the high-way management area.The distinction made between the three planning concepts employed hereÐavoidance,mitigation,com-pensationÐdeviates from current international termi-nology.This describes`mitigation'as any activity that avoids,minimizes,recti®es,reduces or compensates for the e ects of environmental damage(NEPA,1970; National Research Council,1992).However,our con-cepts stress the three fundamentally di erent approa-ches to counteracting the impacts of a development. Within this framework,`mitigation'contracts the NEPA interpretation to`minimizing,rectifying and reducing'e ects.The terms`avoidance'and`compen-sation'are thus taken to refer to two speci®c issues,and to bypass the compound term`compensatory mitigation'(cf.Bedford,1996).This article focuses on the problems and solutions associated with compensa-tion measures in the stricter sense de®ned above.3.E ects of highways on natureDevelopments generally a ect ecological values by modifying(abiotic)habitat conditions,which in turn in¯uence the abundance and distribution of plant and animal species in the impacted areas.Ecological com-pensation may require no-net-loss of habitat conditions (cf.Adamus et al.,1987),of habitat types(US Fish and Wildlife Service,1980),of species populations(Nilsson and Grelsson,1995),of populations of species groups (e.g.ecotopes for vegetation:Runhaar and Udo de Haes,1994),or of ecological functions(Brinson and Reinhardt,1996),all to the extent that they have ecolo-gical signi®cance or characterize a speci®c ecological site.Before considering the planning and realization of compensation measures(see Sections4and5),we dis-tinguish three primary e ects of highways on nature in terms of changed habitat conditions,viz.the loss, degradation and isolation of habitat(Fig.1).3.1.Habitat lossThere is strong evidence that habitat loss is a problem for species in many habitats,implying serious threats to local and regional populations(cf.Reed,1995;Thomas, 1995).Between the mid-1970s and mid-1980s annual wetland losses in the USA due to infrastructure amounted to about1050km2(Mitchell,1992),i.e.0.02%of rural land in the USA.Over the period1980±1993construction of Dutch rural metalled roads (including verges and road ditches)caused about180 km2of habitat loss,an annual loss of0.04%of rural land in the Netherlands(Central Statistical O ce, 1996).3.2.Habitat degradationAlthough habitat patches remain physically accessible to species,the construction and use of highways may lead to a decline in habitat quality in zones adjacent to the infrastructure.This decline may be due to noise, visual disturbance(e.g.illumination),changes in water table and microclimate,and the spread of toxic sub-stances mainly by air and water pollution.These quali-tative e ects may result in decreased densities of species sensitive to the development,as is the case,forexample, Fig.1.Distinguished e ects of highways on nature(adapted from:Cuperus et al.,1996).42R.Cuperus et al./Biological Conservation90(1999)41±51with woodland and meadow-bird populations exposed to the noise of car tra c(Reijnen et al.,1995,1996).3.3.Habitat isolationInfrastructure may lead to a reduced exchange of species between populations,as a result of increased landscape resistance through barrier e ects,and higher mortality rates through fauna casualties(cf.Andrews, 1990;Saunders et al.,1991).Habitat isolation under-mines the persistence of stable(meta)populations,in which local extinction and recolonization are well-balanced.As metapopulation dynamics are complex,it is still scarcely feasible to make a quantitative assessment of the habitat isolation e ects of infrastructure.Extinction thresholds and minimal viabilities of(meta)populations of single species have been demonstrated in theoretical models(Bascompte and Sole,1996;Hanski et al.,1996), but appear di cult to prove quantitatively in realistic situations(Opdam et al.,1994).This makes it all the more logical to adopt multiple-species approaches. Initial attempts at quantitative assessment are currently in progress in the context of introducing infrastructure-related compensation measures in single-species meta-population models(cf.van Apeldoorn,1997). Secondary e ects of highways,i.e.on species(cf.Fig.1),are dependent on both species and landscape char-acteristics.The role of species characteristics is illu-strated by(1)barrier e ects decreasing and mortality e ects increasing with increasing mammal size(Ver-boom,1996),and(2)specialist species being more vul-nerable to development than generalists(Andre n,1994) or species with a restricted range(Simberlo ,1994). On the other hand,landscape characteristics also determine the stability of populations:as more habitats are fragmented,the persistence of populations becomes increasingly dependent on the spatial arrangement and decreasingly dependent on the total number of suitable habitats(Andre n,1994).4.Planning principles behind ecological compensation in The NetherlandsRecent experiences in the Dutch highway projects provide opportunities for developing a new approach in which the di erent types of ecological compensation can be better combined with highway planning.The type of ecological compensation to be adopted depends on two aspects(e.g.Brinson and Reinhardt,1996):(1)the degree of equivalency of habitats or species(in-kind versus out-of-kind compensation),and(2)the location of the compensation site relative to the development site (on-site versus o -site compensation).In-kind compen-sation involves replacement with the same habitats,species or functions;out-of-kind compensation involves replacement with alternative habitats,species or func-tions.On-site and o -site compensation are de®ned here as being within and outside the e ect zone of the high-way,respectively.The width of this zone depends on the cause of habitat degradation(e.g.noise load,change of water table,etc.).4.1.In-kind compensation measures4.1.1.Habitat lossThe method used to reverse the e ects of habitat loss is creation of habitat patches of the same size and qual-ity via(on-site or o -site)in-kind compensation(Fig.2). Upgrading existing habitat may also be e ective as a secondary approach.Generally,the longer time required for the habitat to develop,the more di cult it will be to compensate for impacts.Long established and ancient habitats can scarcely be replaced,if at all (Anderson,1994).4.1.2.Habitat degradationNo-net-loss of habitat degradation is preferably achieved by upgrading habitats.In-kind compensation measures should aim at restoring the ecosystem, expressed in terms of the densities of(selected)species prior to the development(Fig.3A).Depressed water tables may be compensated for by raising groundwater levels o -site,providing suitable conditions for ground-water-dependent vegetation.On-site(in-kind)compen-sation for the impact of elevated noise loads can only be achieved by intervening in other habitat conditions,as habitat quality is determined by a multiple set of habitat conditions.Decreased meadow-bird densities insub-pensation for impacts of habitat loss.R.Cuperus et al./Biological Conservation90(1999)41±5143optimal habitat patches due to tra c noise may be compensated for basically within the e ect zone either by raising the water table or by introducing a new management regime to render the a ected habitat more attractive to meadow birds (cf.de Jong,1977;Fig.3B).For highly sensitive species such measures are more e ective o -site,as these species will probably persist in avoiding the impacted zones.4.1.3.Habitat isolationCompensation for isolation e ects should aim to o -set decreased dispersal rates and increased mortality rates.Appropriate measures are (a combination of)enlarging and upgrading habitats or increasing the con-nectivity of isolated habitat patches.An example of such a combination of measures associated with high-way construction is concurrent closure of the 'lower-level'road network (e.g.trunk roads)to motorized tra c.This measure aims to achieve not only a decrease in the overall noise load of habitats and numbers of fauna casualties,but also continuity of suitable habitat patches.New patches may be developed and attached spatially to or located within existing nature areas,thusforming larger units with a potentially greater number of species and individuals.Alternatively,or in addition,new patches may be located so as to serve as links between the core areas of species,thus reinforcing or creating ecological corridor functions.This strategy does not appear particularly e ective for old-growth forest plants,however (Grashof-Bokdam,1997).Gen-erally,compensation is more e ective in or close to the core areas of species than in areas at the edge of their distribution range.If infrastructure is rendered more permeable for wildlife movements through mitigation measures (e.g.fauna tunnels and ecoducts),then compensation mea-sures in the vicinity of the highway may increase the connectivity of habitats on either side of the infra-structure.Such a strategy requires e ective mitigation as well as compensation sites located within the e ect zone of the infrastructure (Fig.4A).From metapopulation perspectives,however,intensifying habitat-network components on just one side of the highway maysome-pensation for e ects on habitat isolation.A.Reference situation (without highway)bination of on-site and on-site compensation through enlarging (a),upgrading (b),and connecting (c)habitats,requiring an e ective mitigation.C.O -site compensation through enlarging and upgrading habitats,the compensation sites located at one side of the highway,thus avoiding mitigationmeasures.pensation for impacts of habitat degradation.A.In-kind compensation derived from dose-e ect responses (curve adapted from:Reijnen et al.,1995).B.Close in-kind compensation in the e ect zone of the highway for degradation of meadow bird habitat,by interven-ing on other habitat conditions.Realization of the infrastructure and the compensation measures are not successive in practice,but sepa-rated here for exempli®cation.44R.Cuperus et al./Biological Conservation 90(1999)41±51times yield greater bene®ts,as this avoids the risks of ine ective mitigation(Fig.4B).4.2.Out-of-kind compensation measuresUnlike in-kind compensation,out-of-kind compensa-tion provides scarcely any scope for objective identi®-cation of equivalent habitats or species,since there is seldom any strict ecological relationship between impacted and trade-o habitats.As a rule of thumb, habitats may be traded by employing a nature con-servation strategy in which habitat exchange is per-mitted only within the context of equivalent ecosystem or management properties.In the Dutch situation this would imply that habitat exchange to compensate for impacts on the National Ecological Network is per-mitted within a number of individual network units,but not between these units(Table1).5.Realization of ecological compensation in The Netherlands5.1.Realization and evaluation of compensation measuresCompensation measures should support current nat-ure management policies and should be physically loca-ted outside areas where speci®c nature-policy objectives are already operational,for example the core areas of the Dutch National Ecological Network(MANF, 1990).Compensation objectives should take account of the habitat conditions and the actual habitat qualities of the site prior to acquisition,design and management (the`pre-compensation site')as well as the long-term quality of the site to be pursued under the terms of current policies.In practice,sites for ecological com-pensation are determined by a combination of adminis-trative goals set by the competent authorities,the availability of suitable soil conditions and other criteria determining the ecological potentials of the site(cf. MTPW,1995).Once the site or sites are acquired, design and management plans must be drawn up if necessary on the basis of the habitat-quality objectives envisaged and subsequently implemented.Ideally,these plans should be operative prior to highway construc-tion,thus allowing compensation sites to be colonized by source-habitat fauna and vegetation through dis-persal or,in the case of vegetation,via seed banks (Bakker et al.,1996).Purchased compensation grounds will be transferred to well-equipped conservation trusts.5.2.Legislation and instrumentsIn the Netherlands,the compensation principle is the policy line adopted by the national government.There is not yet any statutory legislation in place through which the compensation principle can be enforced by law if necessary,pensation measures are instead to be realized on a voluntary basis,rooted in agreements between a ected parties.This voluntary character has several operational nd-use changes are permitted only on the basis of authorized zoning plans,for which municipalities bear prime responsibility.Highway initiators and municipalities must therefore agree upon implementation of permit-related measures in zoning plans,thus furnishing the initiators with legal grounds for the expropriation of land for compensation purposes.Under the terms of these agreements,land may be acquired through pur-chase from individual owners.In addition,though, project initiators may otherwise create opportunities for land to be exchanged among two or more cooperating owners,to achieve better spatial organization of the compensation lands.In order to accomplish this,the initiator must then himself own sites in order to act as a negotiating party in the real-estate market.As land-owners will sell real estate on a non-committal basis only,opportunities for initiators exist mainly in(rural) regions that are economically weak.In such regions land-owners are more likely to be willing to sell proper-ties since they do not depend entirely on revenues from their lands.In the case of potential purchase of com-pensation sites by the initiator,it is favourable to tie in with existing spatial plans,such as ongoing land re-allotment projects.Alternatively,one may initiate new plans,for example by using the concept of Land Adaptation(aanpassings-Table1Features of the four units of the Dutch`National Ecological Network'(adapted from:Bal et al.,1995)Nearly natural unit Managed natural unit Semi-natural unit Multi-functional unitConservation strategy No human interaction,only designand external maintenance Imitation and stimulation ofspeci®ed processesMaintenance of avegetation stageJoint use of area functionsSuccession stage Several stages Several stages One stage/mosaic One stageExamplesÐNatural woodlandÐTidal waters nature reserves such as:ÐMultifunctional woods ÐDynamic dunesÐRiver beds,basins and banksÐHeathlandsÐFlowerÐrich arable landsÐSea,incl.coastal zonesÐSandÐdriftsÐPeat bogsÐWaterÐcatchment areasÐOligotrophic grasslandsÐMilitary exercise areasR.Cuperus et al./Biological Conservation90(1999)41±5145inrichting),developed under the Dutch Land Use Act (O cial Gazette,1985)to compensate for the adverse e ects of large-scale infrastructure works on agri-cultural,nature and recreation functions(MANF, 1993).5.3.CostsCompensation costs are all those involved in trans-forming a pre-compensation site to one with suitable long-term habitat qualities.Acquisition costs are deter-mined primarily by the regional availability of real estate.Site design and long-term management costs are variable and depend on actual and potential habitat conditions,the long-term quality objectives being pur-sued,and the time available to develop the site.Supple-mentary to the design and management costs,the Dutch government has added a variable per-hectare quality allowance for compensation sites,to be paid by the initiator.The exact allowance depends on the replace-ability of the lost habitat quality;it is intended for pre-paratory work such as top-soil removal,for example. Quality allowances,donated by the initiator,will be awarded to the conservation trust involved through the so-called`Green Fund'(MANF,1995).The total costs of the mitigation and compensation measures have been computed in some detail for several actual highway projects.The estimated costs of o -setting the adverse impacts on nature associated with construction of highway A50between Eindhoven and Oss(30km)run to5.0%of total construction costs of the highway(mitigation US$11.5million,compensa-tion US$5million,construction US$330million);in the case of highway A73South(40km)5.8%of con-struction costs are earmarked for mitigating(US$10 million)and compensating for(US$14.5million) adverse impacts on nature(MTPW,1995,1997,respec-tively).In both projects,long-term management is incorporated in the compensation costs as a one-o lump sum capitalization over a period of10years.If compensation measures are physically unfeasible, owing to non-cooperation on the part of landowners or municipal authorities or an absence of suitable habitat conditions,the government agency involved imposes a ®nancial charge,to be donated to the Green Fund.This charge can be used to®nance projects that would not otherwise have been realized,and must be proportional to the costs of restoring or recreating the ecological values impacted by the development.Because measures ®nanced by the charge are unrelated to the ecological and spatial aspects of the development in question,a physical no-net-loss situation will never be achieved. The®nancial contribution should therefore be post-poned as long as possible,since it can readily be inter-preted as a`redemption'of the development by the initiator.In the context of Dutch highway planning,the intention thus far has been for the portion of the ear-marked compensation costs that could not be invested in compensation measures until after opening of the highway to be treated as®nancial contribution(MTPW, 1995;1997).6.Discussion6.1.Dilemmas in planning and realizing compensation measures6.1.1.Planning aspects of ecological compensationOn-site,in-kind compensation will generally prevail over the other alternatives.This option is more likely to o set the lost functions of impaired sites,since habitat conditions are then already in place(Brinson and Rheinhardt,1996),the potential for minimizing disrup-tion of remaining ecological functions will be higher (Race and Fonseca,1996)and compensation sites are often part of a larger system(Hashisaki,1996a). Nevertheless,there are also motives for adopting o -site compensation:in this way larger ecosystems can be connected(Hashisaki,1996a)and better results achieved,since the compensation sites are not adversely in¯uenced by the infrastructure itself(Mitsch and Wil-son,1996).General standards and guidelines for choosing between`on-site/o -site'and`in-kind/out-of-kind'com-pensation cannot be given,as these depend on the availability of suitable compensation sites and must therefore be determined on a case-by-case basis.In the USA`mitigation banking'has recently been introduced, a scheme whereby large areas of'reserve land'are built up from which initiators can buy a compensation site once a project has gained approval(cf.Glick®eld et al., 1995;Zedler et al.,1997).Banking of credits in advance favours acceleration of the approval procedure,apart from the`redemption'issue,because the compensation site is acquirable;furthermore,it lowers mitigation and compensation costs,and increases compensation e -ciency,as one large compensation site avoids the frag-mentation associated with smaller sites(Hashisaki, 1996b).These argumentsÐand particularly the fact that acquisition of Dutch real estate will be di cult in some regionsÐmake it worth considering the application of mitigation banking in(parts of)the Netherlands. Equivalences in species diversity and the regional, national or even international rarity of habitats and species may form the basis of out-of-kind compensation (Rossi and Kuitunen,1996).Although these criteria may be appropriate tools for the design and manage-ment of replaceable nature areas,it should be realized that in assessing ecosystem functions,compensation ratios(i.e.the ratio of replaced to lost area)and inter-change of habitats are based on institutional mandate46R.Cuperus et al./Biological Conservation90(1999)41±51or public input(Abbruzzese and Leibowitz,1997). Compensation resulting from habitat trade-o should be consistent with the composition of the landscape. Calculation of the theoretical in-kind compensation costs that need to be incurred to obtain a standard for out-of-kind compensation,as exempli®ed by Kiemstedt von et al.(1996),can serve as a practical tool for trading dissimilar habitats or species.6.1.2.Realization and evaluation of compensation measuresSuccessional trends of habitat types are generally predictable only in broad terms(cf.Atkinson et al., 1993).A compensation plan should therefore be based on processes(e.g.erosion,sedimentation,humus for-mation,grazing)and species groups as representatives for the ecosystem that it is intended to develop.In such a compensation plan,initiators and conservation trusts shouldÐprior to transfer of landsÐreach agreement on mutual responsibilities,compensation objectives,valid monitoring activities(Howald,1996)and the one-o lump sum to be paid to the managing body(Box,1996). Complex issues involving timing and responsibility arise,however,whether initiators are freed of their obligation to meet no-net-loss objectives at the moment of transfer,or after a substantial period,once biological evaluations and adjustments have been carried out. The Dutch government should become intently aware of potential pitfalls associated with compensation pro-jects.Practical American and German experience indi-cates that compensation measures may be relatively ine ective for several reasons:lack of proper ecological input,incorrect habitat conditions at compensation sites,inappropriate site design and management,inade-quate compliance with compensation requirements on the part of the initiator,inadequate liaison of autho-rities and initiators with environmental groups,and lack of an accurate registration system allowing the control-ling authority to adequately supervise compliance(cf. Ho mann and Ho mann,1990;Race and Fonseca, 1996).Failures due to ecological factors and insu cient compliance can be minimized by introducing evaluation and monitoring criteria in the compensation plan,and by attaching stringent compliance conditions to a bank guarantee,including contingency measures for use in the event of unsatisfactory results(cf.Treweek and Thompson,1997).The guarantee might be signi®cantly higher than the estimated cost of restoration or recrea-tion of the ecological values,stimulating the initiator to meet his obligations(cf.Province of Overijssel,1998).If the compensation measures fail to comply with the per-mit conditions,the guarantee will accrue to the relevant authority.This will then be responsible for guaranteeing that compensation is properly made.It should be noted that compensation credits are probably sensitive to economic cycles(Glick®eld et al.,1995).This will never provide complete guarantee in practice that compensa-tion plans will be eventually realized(Hashisaki,1996b). In the Netherlands,registration and progress of com-pensation plans will be supervised by provincial autho-rities(e.g.Province of Overijssel,1998;Province of Zuid-Holland,1997),since the national government has decentralized policy implementation.Another aspect of achieving compensation objectives is the role of public interests as related to speci®c com-pensation projects.In some cases surplus value can be created by moulding`win±win'situations in which compensation objectives are combined with other regional nature conservation projects,and with agri-cultural,recreational or other landscape functions. When such integrated solutions can be designed to achieve surplus value,they may enjoy greater public support and thus be more sustainable over time and space,than,for example,nature reserves enforced by expropriation as a means of compensation.6.1.3.Legislation and instrumentsLegislative embodiment of the compensation princi-pleÐas in the US Clean Water Act and the German Eingri sregelungÐis under discussion in the Nether-lands.The Dutch government is to decide in the near future whether or not to give the compensation princi-ple a legislative footing(MANF and MHPE,1993; MANF,1997).Serious consideration should be given to developing more appropriate legislation on compensa-tion in the Netherlands to provide due guarantees to society that no-net-loss will indeed be achieved,in the ®nal case by citizens®ling a notice of appeal.Such a legal,national basis may be provided through adapta-tion of the Nature Conservation Act(O cial Gazette, 1967)or Environmental Planning Act(O cial Gazette, 1965).Although still premature at the moment,legisla-tion may include provisions for audits,®nes and civil penalties in cases where a compensation plan is not ultimately achieved(cf.Race and Fonseca,1996). Furthermore,as a procedural step within the Routing Act(O cial Gazette,1994),decisions on highway routes are based on elaboration of the`preferential' route,i.e.the alternative intended to be chosen by the Minister of Transport,Public Works and Water Man-agement.To date,in the preferential alternative and the routing decision,the mitigation(not compensation) measures associated with the route are to be speci®ed in terms of exact spatial occupation.Under the terms of the Routing Act,municipalities unwilling to act on a voluntary basis can be obliged to adapt their zoning plans to the development,thus giving initiators a legal basis to expropriate land for highway construction andÐto a certain extentÐmitigation measures.If the government were empowered to incorporate the com-pensation sites into the routing decision(which is not the case at present),a legal basis would be procured forR.Cuperus et al./Biological Conservation90(1999)41±5147。

托福阅读tpo42R-1原文+译文+题目+答案+背景知识

托福阅读tpo42R-1原文+译文+题目+答案+背景知识

托福阅读tpo42R-1原文+译文+题目+答案+背景知识原文Geographic Isolation Of Species①Biologist Ernst Mayr defined a species as“an actually or potentially interbreeding population that does not interbreed with other such populations when there is opportunity to do so.”A key event in the origin of many species is the separation of a population with its gene pool(all of the genes in a population at any one time)from other populations of the same species,thereby preventing population interbreeding.With its gene pool isolated,a separate population can follow its own evolutionary course.In the formation of many species,the initial isolation of a population seems to have been a geographic barrier.This mode of evolving new species is called allopatric speciation.②Many factors can isolate a population geographically.A mountain range may emerge and gradually split a population of organisms that can inhabit only lowland lakes,certain fish populations might become isolated in this way.Similarly,a creeping glacier may gradually divide a population,or a land bridge such as the Isthmus of Panama may form and separate the marine life in the ocean waters on either side.③How formidable must a geographic barrier be to keep populations apart?It depends on the ability of the organisms to move across barriers.Birds and coyotes can easily cross mountains and rivers.The passage of wind-blown tree pollen is also not hindered by such barriers,and the seeds of many plants may be carried back and forth on animals.In contrast,small rodents may find a deep canyon or a wide river an effective barrier.For example,the Grand Canyon,in the southwestern United States,separate the range of the white-tailed antelope squirrel from that of the closely related Harris’antelope squirrel.Smaller,with a shorter tail that is white underneath,the white-tailed antelope squirrel inhabits deserts north of the canyon and west of the Colorado River in southern California. Harris'antelope squirrel has a more limited range in deserts south of the Grand Canyon.④Geographic isolation creates opportunities for new species to develop,but it does not necessarily lead to new species because speciation occurs only when the gene pool undergoes enough changes to establish reproductive barriers between the isolated population and its parent population.The likelihood of allopatric speciation increases when a population is small as well as isolated,making it more likely than a large population to have its gene pool changed substantially.For example,in less than two million years,small populations of stray animals and plants from the South American mainland that managed to colonize the Galapagos Islands gave rise to all the species that now inhabit the islands.⑤When oceanic islands are far enough apart to permit populations to evolve in isolation,but close enough to allow occasional dispersions to occur,they are effectively outdoor laboratories of evolution.The Galapagos island chain is one of the world's greatest showcases of evolution.Each island was born from underwater volcanoes and was gradually covered by organisms derived from strays that rode the ocean currents and winds from other islands and continents. Organisms can also be carried to islands by other organisms,such as sea birds that travel long distances with seeds clinging to their feathers.⑥The species on the Galapagos Islands today,most of which occur nowhere else, descended from organisms that floated,flew,or were blown over the sea from the South American mainland.For instance,the Galapagos island chain has a total of thirteen species of closely related birds called Galapagos finches.These birds have many similarities but differ in their feeding habits and their beak type,which is correlated with what they eat.Accumulated evidence indicates that all thirteen finch species evolved from a single small population of ancestral birds that colonized one of the pletely isolated on the island after migrating from the mainland,the founder population may have undergone significant changes in its gene pool and become a new ter,a few individuals of this new species may have been blown by storms to a neighboring island.Isolated on this second island,the second founder population could have evolved into a second new species,which could later recolonize the island from which its founding population emigrated.Today each Galapagos island has multiple species of finches, with as many as ten on some islands.译文物种的地理隔离①生物学家恩斯特·迈尔将物种定义为“实际上或潜在的杂交种群,在有机会的情况下不会与其他同类种群杂交。

九年级地理环境英语阅读理解30题

九年级地理环境英语阅读理解30题

九年级地理环境英语阅读理解30题1<背景文章>The tropical rainforest is one of the most fascinating and important ecosystems on Earth. It is characterized by its dense vegetation, high levels of biodiversity, and unique climate.The rainforest is home to an incredibly diverse range of plant and animal species. Many of these species are found nowhere else in the world. The canopy of the rainforest is a complex network of branches and leaves that provides a habitat for countless animals, including monkeys, birds, and insects. The understory is also rich in life, with a variety of plants and smaller animals.The tropical rainforest plays a crucial role in maintaining the balance of the Earth's ecosystem. It helps regulate the climate by absorbing carbon dioxide and releasing oxygen. It also influences weather patterns and provides important resources such as clean water and fertile soil.However, the tropical rainforest is facing numerous threats. Deforestation is one of the most significant challenges. Logging, agriculture, and urbanization are all contributing to the destruction of the rainforest. This not only leads to the loss of biodiversity but also has a negative impact on the climate and the livelihoods of local communities.To protect the tropical rainforest, various measures can be taken. Conservation efforts should focus on sustainable logging practices, protecting wildlife habitats, and promoting reforestation. Education and awareness-raising are also essential to encourage people to take action and support rainforest conservation.1. What is one of the characteristics of the tropical rainforest?A. Sparse vegetation.B. Low levels of biodiversity.C. Unique climate.D. Few animal species.答案:C。

小学上册第十二次英语第六单元测验卷(有答案)

小学上册第十二次英语第六单元测验卷(有答案)

小学上册英语第六单元测验卷(有答案)考试时间:80分钟(总分:110)B卷一、综合题(共计100题共100分)1. 选择题:What do we call a baby lion?A. CubB. CalfC. KitD. Pup答案:A2. 听力题:I like to ___ (help) with chores.3. 填空题:My family always goes __________ during summer. (旅行)4. 填空题:The _____ (阳光) is essential for photosynthesis.5. 填空题:I enjoy listening to ________ music.6. 填空题:My sister loves __________ (动物) and wants to be a vet.7. 填空题:A ________ (植物研究项目) can yield results.8. 选择题:What do you call a collection of written works?A. AnthologyB. CompilationC. ArchiveD. All of the above答案:DThe _____ (conifer) has needle-like leaves.10. 填空题:The __________ is a large city known for its skyscrapers. (纽约)11. 填空题:I have a ________ (日记) to write in.12. 选择题:What do we call the act of raising animals for food?A. AgricultureB. HorticultureC. Animal HusbandryD. Gardening答案:C13. 选择题:What do we use to write?A. BrushB. PencilC. SpoonD. Fork答案:B14. 填空题:My friend loves to engage in __________ (志愿活动).15. 选择题:What do we call a large area of flat land?A. HillB. PlainC. ValleyD. Mountain答案: B16. 填空题:I like to help organize _______ (活动) at school. It’s a great way to meet new _______ (朋友).17. 填空题:A ______ (种植计划) requires careful thought.18. 填空题:A bunny's feet are very ______ (强壮).What is the capital of Germany?A. MunichB. BerlinC. FrankfurtD. Hamburg20. 听力题:The chemical formula for sodium carbonate is __________.21. 听力题:The baby is sleeping ___. (quietly)22. 填空题:The ________ (绿色植物) are important for oxygen.23. 选择题:What do we call the device we use to see distant objects?A. MicroscopeB. TelescopeC. BinocularsD. Magnifying glass24. 选择题:How many colors are in a standard rainbow?A. FiveB. SixC. SevenD. Eight答案:C25. 听力题:Photosynthesis is the process by which plants make their own ________.26. 填空题:The walrus has whiskers on its ________________ (脸).27. 听力题:__________ is the substance that dissolves in a solution.28. 选择题:What do you call the person who sings?A. DancerB. PainterC. SingerD. WriterThe capital of the Cayman Islands is __________.30. 听力题:She _____ (loves/love) chocolate cake.31. 填空题:The first person to win the Nobel Prize in Physiology was _______. (埃米尔·冯·贝尔)32. 听力题:We are going to ________ a picnic.33. 填空题:I like to collect ______ (邮票).34. 选择题:What do we use to cut paper?A. TapeB. GlueC. ScissorsD. Ruler答案: C. Scissors35. 填空题:The __________ (寒冷) climate affects our activities.36. 听力题:The amount of matter in an object is referred to as its _____ (mass).37. 填空题:My birthday is in the month of ________.38. 填空题:The ________ was a significant event in the history of technology.39. 填空题:My cousin is a great __________ (倡导者).40. 听力题:The Rosetta Stone helped decode _______ hieroglyphs.41. 选择题:What is the name of the famous explorer who discovered America?A. Marco PoloB. Christopher ColumbusC. Ferdinand MagellanD. Vasco da Gama42. 听力题:It is _____ (冷) outside today.43. 选择题:What is the name of the popular board game where you connect words?A. ScrabbleB. BoggleC. ScattergoriesD. Hangman答案: A44. 听力题:A group of fish swimming together is called a __________.45. 填空题:We can _______ to the zoo this weekend.46. 听力题:The tree is _______ (covered) in blossoms.47. 选择题:What is the name of the ocean between Africa and Australia?A. AtlanticB. PacificC. IndianD. Arctic答案:C48. 听力题:The ______ grows in forests.49. 听力题:Solar panels convert sunlight into ______.50. 填空题:My __________ (玩具名) is my trusty __________ (名词).51. 选择题:What is the name of the animal that can jump and has a pouch?A. KangarooB. PandaC. LionD. KoalaWhat do we call a young squirrel?A. KitB. PupC. BabyD. Fry答案:C. Baby53. 听力题:The Earth's crust is rich in ______ elements.54. 听力题:The elephants are _____ (big/small) animals.55. 填空题:I like to ride my ______.56. 听力题:A ______ has unique patterns on its skin.57. 听力题:I found a ________ on the ground.58. 选择题:How many countries are in the European Union?A. 27B. 28C. 29D. 30答案: A59. 填空题:Plants are essential for maintaining ______ balance on Earth. (植物对维持地球的生态平衡至关重要。

中国饮食文化内涵英语介绍

中国饮食文化内涵英语介绍
Culinary Diversity
From the spice food of Sichuan to the seafood dishes of Guangdong, the diverse culinary styles reflect the regional characteristics and cultural heritage Understanding these regional differences is essential for a deeper application of Chinese food culture
Chinese food culture also includes the use of medical foods to maintain or restore health Herbs and other eligible individuals used in traditional dishes have thermal properties that are believed to help prevent or treat variant illnesses
02
The Characteristics of Chinese Food Culture
Diversity of talents
Chinese food culture is rich in diversity, utilizing a wide range of talents from both land and sea Traditional Chinese cuisine often involves corporate meals, seafood, vegetables, fruits, and grains, creating complex flavors and textures

学术英语社科类unit原文及翻译

学术英语社科类unit原文及翻译

Cultural Globalization1. Much of the early development of different languages, customs, and otherdiverse aspects worldcultures resultedfromthe isolation of groups of people from one another. It is not surprising , then, that a degree of cultural amalgamation has occurred as improved transportation and communication have brought people of various societies into ever more frequent contact . Analyzing the blurring of cultural differences inevitably includes a great deal about fast food, basketball, rock music,and other such aspects of pop culture,but such analysis does not trivialize the subject,. Instead , a long standing bottom up line of political theoryargues that the world`s people can build on commonplace interactions and increasing cultural commonalities that engender familiarity with and confidence in one another to create a global civil society that might evolve into a global nation. By the same process, if transnational civil societies develop, then regional andevenglobal schemes of governance could conceivably form and supplement or supplant the territorial state. Scholars who examine the bottom-up process of transnational integration look for evidence in such factors as the flow of communications and commerce between countries and the spread across borders of what people wear, eat, and do for recreation.1、不同语言、风俗习惯以及其他不同的文化背景下,世界文化的早期发展,是从彼此分离的人群中产生的。

高三英语艺术批评标准练习题30题

高三英语艺术批评标准练习题30题

高三英语艺术批评标准练习题30题1.In the painting, the colors are vivid and the brushstrokes are bold. The artist's use of ______ is remarkable.A.techniqueB.styleC.methodD.way答案:A。

选项A“technique”表示技巧、技术;选项B“style”是风格;选项C“method”是方法;选项D“way”是方式。

在描述绘画中艺术家对某种东西的运用很出色,这里指的是绘画技巧,所以选A。

2.The sculpture is known for its delicate ______.A.detailB.patternC.shapeD.form答案:A。

选项A“detail”是细节;选项B“pattern”是图案;选项C“shape”是形状;选项D“form”是形式。

雕塑以其精致的细节而出名,所以选A。

3.The music piece is full of emotional ______.A.expressionB.feelingC.sensationD.impression答案:A。

选项A“expression”表示表达、表情;选项B“feeling”是感觉;选项C“sensation”是感觉、知觉;选项D“impression”是印象。

音乐充满情感表达,所以选A。

4.The dance performance shows great ______ of movement.A.graceB.beautyC.eleganceD.fluidity答案:D。

选项A“grace”是优雅;选项B“beauty”是美丽;选项C“elegance”是高雅;选项D“fluidity”是流畅性。

舞蹈表演展现出很大的动作流畅性,所以选D。

5.The play is praised for its powerful ______.A.dialogueB.plotC.characterD.theme答案:D。

翻译——精选推荐

翻译——精选推荐

The significance of froth stability in mineralflotation — A review中文翻译******班级:化工08-1班学号:**********The significance of froth stability in mineral flotation — A review矿物浮选中泡沫稳定性的意义-评论Abstract摘要This paper presents a review of the published articles related to froth stability and its importance in mineral flotation. Froth structure and froth stability are known to play a significant role in determining the mineral grade and recovery achieved in a flotation operation. Froth stability is depending not only on the type and concentration of the frother but also on the nature and amount of the particles present in the system. To date, there is no specific criterion to quantify froth stability although a number of parameters are used as indicators of froth stability. Linking froth stability to the metallurgical performance is also challenged.文章综述了已发表文章涉及矿物浮选过程中泡沫稳定性及其重要性的相关观点。

A PUMP

A PUMP

专利名称:A PUMP发明人:KNOWLES, Albert, Henry Westbrook 申请号:EP86906376.0申请日:19861020公开号:EP0243435A1公开日:19871104专利内容由知识产权出版社提供摘要: Pump having a chamber provided with a deformable separation. This separation is mounted so as to be capable of upward and downward movement in the chamber to expel the pump fluid. In the upper part of the chamber, the separation is deformed under the effect of its own weight and moves down through the water column to be expelled from the pump. In the lower part of the chamber, the separation opens as air is introduced in the separation to trap water above. The air introduced traces the separation and causes the expulsion of the water pump above the separation. In the upper part of the chamber, the air is released, the separation and deforms the pumping cycle is repeated.申请人:SAVE THE CHILDREN地址:Mary Datchelor House, 17 Grove Lane, Camberwell London SE5 8RD GB国籍:GB更多信息请下载全文后查看。

注意力缺陷多动障碍(ADHD)相关说明书

注意力缺陷多动障碍(ADHD)相关说明书

ATTENTION DEFICIT HYPERACTIVITY DISORDERKEY FACTS■Attention deficit hyperactivity disor-der (ADHD) is one of the most com-monly diagnosed mental disordersin U.S. children and adolescents,affecting up to 3 to 5 percent ofschool-age children (Cantwell,1996; Wolraich et al., 1996).■There is no single diagnostic tool forADHD. To diagnose the disorder, ahealth professional considers achild’s or adolescent’s history andsymptoms and rules out otherpotential causes of inattention,hyperactivity, and impulsivity.■The exact cause of ADHD is notknown. Children and adolescentswith ADHD may have low levels ofcertain neurotransmitters in brainregions controlling attention andimpulsivity.■Many children and adolescents withADHD improve as they grow up.One-third have no symptoms bythe time they reach adulthood(Cantwell, 1996; Dulcan, 1997).■Children and adolescents withADHD are at risk for school under-performance, social isolation, andlow self-esteem.DESCRIPTION OF SYMPTOMSInattention, hyperactivity, and impulsivity problems fall along a continuum. For some children and ado-lescents such symptoms do not impair functioning enough to warrant a diagnosis of ADHD, but the symp-toms nevertheless cause frustration in the child or adolescent or those near her, or impede her learning to some degree. DSM-PC describes these inattention and hyperactivity/impulsivity problems as follows.When a child’s or adolescent’s inattention and/or hyperactivity and impulsivity occur in many different settings over a long period and impair his functioning, this indicates that he may have a disorder rather than a problem. In order to meet the criteria for ADHD, these symptoms need to have been present before age 7.Further information on the diagnosis of ADHD is available in the American Academy of Pediatrics’ clinical practice guide-lines, “Diagnosis and Evaluation of the Child with Attention-Deficit/Hyperactivity Disorder” (American Academy of Pediatrics, 2000); Attention Deficit Hyperactivity Disorder: A Handbook for Diagnosis and Treatment(Barkley, 1998); Diagnosis and Treatment of Attention Deficit Hyperactivity Disorder (ADHD): NIH Consensus Statement(1998); and “Practice Parameters for the Assessment and Treatment of Children, Adolescents, and Adults with Attention-Deficit/Hyperactivity Disorder” (Dulcan, 1997).Description of Symptoms (continued)INTERVENTIONSThese general interventions may help primary care health professionals to identify children and adolescents with ADHD and related problems and to manage their symptoms. (See Bright Futures Case Studies for Primary Care Clinicians:Attention-Deficit/Hyperactivity Disorder: The Restless Pupil [Frazer and Knight, 2001] at http://www.pedicases. org.)Child or Adolescent1.If the school or family expresses concern about achild’s or adolescent’s disruptive behavior orinattention, or if screening questions reveal con-cerns in these areas, further information should be gathered. Scales for assessing ADHD includethe Vanderbilt ADHD Diagnostic Teacher Rating Scale (Wolraich, 1998), SNAP-IV (Swanson,1991), ADHD Rating Scale-IV (DuPaul, 1998), and Conners’ Rating Scales (Conners, 1997). For achild or adolescent to meet the criteria forADHD, his symptoms need to be present in sever-al different settings, including home and school.Therefore, obtaining information from theschool as well as the child or adolescent and fam-ily is critical. Rating scales, report cards, and writ-ten and/or verbal comments from schoolpersonnel about a child’s or adolescent’s presen-tation and performance provide a fuller picture of his academic and behavioral functioning. Psy-choeducational testing should also be considered to identify any learning disabilities that may be affecting academic performance. Obtain a careful social history from the family to identify anyongoing or recent stressors that may also beaffecting the child’s or adolescent’s functioning(American Academy of Pediatrics, 2000). (SeeTool for Health Professionals: Vanderbilt ADHD Diagnostic Teacher Rating Scale, Mental HealthTook Kit, p. 54.)2.Assess for the following other possible underlyingor associated medical or psychosocial concerns:•Low birthweight•Mental retardation•Drug or alcohol exposure in utero•Neurotoxin exposure (e.g., lead poisoning)•Central nervous system infections•Head injury•Thyroid dysfunction•Child abuse and neglect•Foster home placements3.Assess for mood problems and disorders by ask-ing the child or adolescent about his mood, abili-ty to have fun, and sleep. Assess for anxietyproblems and disorders by asking about worries, separation problems, and somatic complaints.Children and adolescents with symptoms ofADHD and depression or anxiety present particu-lar diagnostic and treatment challenges. A mental health professional such as a child psychiatrist,child psychologist, or clinical social worker who engages with a child or adolescent in individual consultation and therapy may be able to helpclarify diagnoses, develop a treatment plan, and stabilize symptoms. Medication interventions fora child or adolescent with ADHD and anxiety ormood symptoms can be complicated. Referral to or consultation with a child psychiatrist or devel-opmental-behavioral pediatrician is recommend-ed. (See Pharmacological Interventions, p. 210.)ADHD4.Children and adolescents with ADHD may also benefit from individual or group therapy that focuses on •Learning impulse control •Building self-esteem •Acquiring coping skills •Building social skills5.Children with ADHD may feel that they are “bad”because of their social and academic difficulties.Adolescents may experience feelings of failure and low self-esteem. Talk with the child or adolescent in developmentally appropriate language about ADHD and its treatment, explaining that you know he does not mean to cause problems but needs help to control his behavior and to focus.6.Encourage the child or adolescent to break diffi-cult tasks up into manageable parts, take short breaks, and write homework assignments in a special notebook.7.Encourage the child or adolescent to pursue his talents and interests (e.g., drawing, learning to play the drums, taking karate classes). Successeswill boost his self-esteem and promote positive interactions with adults and peers.Family1.Parents may feel they are to blame for theirchild’s or adolescent’s behavior problems. High-light the child’s strengths and specific needs, and point out the parents’ skills in supervising and caring for the child or adolescent, even during challenging periods.2.Discuss with parents any concerns they have about ADHD and about handling their child’s or adolescent’s behavior. Help parents give their child or adolescent positive feedback, communi-cate realistic and clear expectations, and set con-sistent and appropriate limits. For children and adolescents with significant behavior problems,consider referring parents to a developmental-behavioral pediatrician or a mental health profes-sional (e.g., child psychiatrist, child psychologist,clinical social worker), who can assist the family in developing a behavior plan for their child or adolescent.3.Encourage parents to establish routines for their child or adolescent to help her learn organiza-tional skills. It may be useful for parents to draw or write the routine and display it at home (e.g.,for a younger child, create a chart that shows brushing teeth, washing face, getting pajamas;for an older child or adolescent, create a chart illustrating the child’s or adolescent’s and fami-ly’s daily and weekly schedule).4.Ask about a family history of ADHD, learning dis-orders, depression, and anxiety. Explain that the family needs to help the child or adolescent com-pensate for ADHD (e.g., by finding activities thatbuild on her interests and strengths) and thatADHD can improve over time.5.Talk with parents about the role of medication intreating ADHD. Explain that it is often helpfulbut is not a cure. Children and adolescents with ADHD benefit most from a combination ofefforts by their family, their school, and healthprofessionals.6.Help family members identify the child’s or ado-lescent’s talents, stressing the importance ofbuilding self-esteem. Physical activities (e.g.,organized sports, biking, dancing, in-line skating, jumping rope, bowling) can help channel highenergy levels in children and adolescents withhyperactivity or impulsivity, and structuredgroup activities can promote social skills. Remind families that safety gear is especially importantfor children and adolescents with ADHD.7.Assess the quality of the relationship betweeneach parent and the child or adolescent, andencourage parents to spend regular time withtheir child or adolescent. For many male children and adolescents with ADHD, time spent playing or engaging in other activities with their father or another positive male role model is especiallyimportant.cate family members about ADHD, and con-nect them with supportive resources, such asChildren and Adults with Attention Deficit/Hyperactivity Disorder (CHADD). Informationabout CHADD can be found on the organiza-tion’s Web site at .9.Refer parents or siblings experiencing high levelsof stress, difficulty coping, or psychiatric symp-toms to a mental health professional such as aclinical social worker, psychologist, or munity and School1.After obtaining appropriate permission, involveteachers, guidance counselors, and school-based health and mental health professionals in assess-ing the child’s or adolescent’s functioning and in implementing a treatment plan.2.Assess for any possible learning disabilities or spe-cial education needs (DuPaul and Stoner, 1994).Public schools are obligated to assess childrenwhose school performance may be impaired by ADHD or a learning disability. For example, achild or adolescent suspected of having ADHDshould receive a functional behavioral assess-ment conducted by a qualified school profession-al (e.g., school psychologist) to help design abehavior modification program for the class-room. Be aware that children and adolescentswith ADHD may be eligible for special education services under the “other health impaired” dis-ability category. These services include the devel-opment of an Individualized Education Program (IEP). (See Tool for Families: Individualized Edu-cation Program [IEP] Meeting Checklist, Mental Health Tool Kit, p. 120.) Some parents may appre-ciate assistance from the primary care health pro-fessional in contacting the school. Considerparticipating in school conferences or IEP plan-ning meetings for the child or adolescent. Ensure that parents know that their child or adolescent may also qualify for services under Section 504 of the Rehabilitation Act. For further informationabout eligibility and services, families can consult the school’s special education coordinator, thelocal school district, the state department of edu-cation’s special education division, the U.S.Department of Education’s Office of Special Edu-cation Programs (/offices/OSERS/OSEP), the Individuals with DisabilitiesEducation Act (IDEA) ’97 Web site (http://www./offices/OSERS/IDEA), or the U.S. JusticeDepartment’s Civil Rights Division (http://www./crt/edo).3.Work with the school to develop a plan to reducedistracting stimuli for the child or adolescent as much as possible and to ensure that expectations are reinforced clearly and consistently. Suggestthat classroom seating be arranged to address the child’s or adolescent’s needs. Talk with theschool about providing children or adolescents with ADHD with extra support at transitiontimes during the school day.4.Encourage teacher-parent communication, andsuggest that the child or adolescent work onimproving organizational skills by keeping a“homework notebook” in which she recordsassignments and in which parents and teachers record ideas, observations, and praise pertaining to her successes. Suggest that homework time be broken up into 10- to 30-minute chunks withshort breaks in between for play or rest.5.For a child or adolescent who is taking medica-tion for ADHD symptoms, contact should bemaintained with teachers and/or other schoolpersonnel (e.g., the school nurse), to obtaininformation about possible changes in the child’s or adolescent’s classroom behavior and academic performance. Because the time course of somestimulant medications (e.g., methylphenidate) is relatively brief, teachers’ input about the medica-tion’s effectiveness is important. Behavior rating scales like the Conners’ Rating Scales (Conners, 1997) can assist teachers in providing informa-tion about behavior change. In addition, possible changes in the child’s or adolescent’s academic performance (e.g., the amount of work complet-ed correctly) should be assessed, as academic per-formance could be improved or deleteriouslyaffected by stimulant medication.6.For children under age 5, intervention servicesmay be available through IDEA. The local school district or the state department of education can provide specific information about availableresources. (See #2, above.)7.ADHD self-help groups such as CHADD can pro-vide information, referrals, and support services.PHARMACOLOGICAL INTERVENTIONSChildren and adolescents with ADHD usually require multiple interventions to address their diffi-culties. It has been shown that pharmacological interventions can be effective in improving func-tioning in children and adolescents with ADHD. Guidelines for considering a medication trial are offered below.•Given the prevalence of ADHD and its respon-siveness to stimulant medication, primary carehealth professionals may consider a medication trial. For further information on the use of med-ications and the treatment of ADHD, see Ameri-can Academy of Pediatrics (2001), Dulcan (1997), Morgan (1999), Spencer et al. (2000), and Wilens (1999). Ongoing communication with the child’s or adolescent’s family and school (followingguidelines for confidentiality) via mechanismssuch as rating scales is essential in monitoring a child’s or adolescent’s response to medications.•Children and adolescents who do not respond toa stimulant trial, who experience adverse effects,or who show evidence of mood or anxiety symp-toms, substance abuse, developmental delays, tic disorders, or significant family stress may becomplicated to treat. Some primary care health professionals feel comfortable treating children and adolescents with ADHD complicated byother associated problems. For those who do not, referral to a developmental-behavioral pediatri-cian, child neurologist, or child psychiatrist isrecommended.Resources for FamiliesChildren and Adults with Attention Deficit/ Hyperactivity Disorder (CHADD)8181 Professional Place, Suite 201Landover, MD 20785Phone: (800) 233-4050, (301) 306-7070Web site: LD OnLineWeb site: (LD OnLine is a service of the Learning Project at WETA, Washington, DC, in association with the Coordinated Campaign for Learning Disabilities.)National Attention Deficit Disorder Association (NADDA)1788 Second Street, Suite 200Highland Park, IL 60035Phone: (847) 432-ADDA (2332)Web site: Selected BibliographyAmerican Academy of Pediatrics, Committee on Quality Improvement, Subcommittee on Attention-Deficit/Hyperactivity Disorder. 2000. Clinical practice guide-line: Diagnosis and evaluation of the child withattention-deficit/hyperactivity disorder. Pediatrics105(5):1158–1170. Web site: http://www.aap.org/policy/ac0002.html.American Academy of Pediatrics, Committee on Quality Improvement, Subcommittee on Attention-Deficit/Hyperactivity Disorder. 2001. Clinical practice guide-line: Treatment of the school-aged child with atten-tion-deficit/hyperactivity disorder. Pediatrics108(4):1033-1044. Web site: /policy/s0120.html.American Psychiatric Association. 1994. Diagnostic and Sta-tistical Manual of Mental Disorders(4th ed.) (DSM-IV).Washington, DC: American Psychiatric Association.American Psychiatric Association. 2000. Diagnostic and Statistical Manual of Mental Disorders(4th ed., textrevision) (DSM-IV-TR). Washington, DC: AmericanPsychiatric Association.Barkley RA. 1998. Attention Deficit Hyperactivity Disorder: A Handbook for Diagnosis and Treatment(2nd ed.). NewYork, NY: Guilford Press.Barkley RA. 2000. T aking Charge of ADHD: The Complete, Authoritative Guide for Parents(rev. ed.). New York,NY: Guilford Press.Biederman J. 1998. Attention-deficit/hyperactivity disor-der: A life-span perspective. Journal of Clinical Psychiatry 59(7Suppl.):4S–16S.Biederman J, Faraone SV, Mick E, et al. 1999. Clinical cor-relates of ADHD in females: Findings from a largegroup of girls ascertained from pediatric and psychi-atric referral sources. Journal of the American Academy of Child and Adolescent Psychiatry38(8):966–975. Cantwell DP. 1996. Attention deficit disorder: A review of the past 10 years. Journal of the American Academy ofChild and Adolescent Psychiatry35(8):978–987. Conners CK. 1997. Conners’ Rating Scales (revised CRS-R, long version). North Tonawanda, NY: Multi-HealthSystems. Phone: (800) 456-3003; Web site: http://www.mhs.co.Diagnosis and treatment of attention deficit hyperactivity disorder (ADHD): NIH consensus statement.1998.16(2):1–37. Web site: /consensus/cons/110/110_intro.htm.Dulcan M. 1997. Practice parameters for the assessment and treatment of children, adolescents, and adultswith attention-deficit/hyperactivity disorder. Journalof the American Academy of Child and Adolescent Psychi-atry36(10Suppl.):85S–121S.DuPaul GJ. 1998. A DHD Rating Scale-IV: Checklists, Norms and Clinical Interpretation.New York, NY: GuilfordPress.DuPaul GJ, Stoner GD. 1994. ADHD in the Schools: Assess-ment and Intervention Strategies.New York, NY: Guil-ford Press.Frazer C, Knight JR. 2001. Attention-deficit/hyperactivity disorder: The restless pupil. In Knight JR, Frazer C,Emans SJ, eds., Bright Futures Case Studies for PrimaryCare Clinicians: Child Development and Behavior.Boston, MA: Bright Futures Center for Education inChild Growth and Development, Behavior, and Ado-lescent Health. Web site: .Jensen PS, Martin D, Cantwell DP. 1997. Comorbidity in ADHD: Implications for research, practice, and DSM-V. Journal of the American Academy of Child and Adoles-cent Psychiatry36(8):1065–1079.Kaplan HI, Sadock BJ. 1995. Comprehensive Textbook of Psychiatry(6th ed.). Baltimore, MD: Williams &Wilkins.Morgan AM, ed. 1999. Attention-deficit/hyperactivity dis-order. Pediatric Clinics of North America46(5).Philadelphia, PA: W. B. Saunders.Spencer T, Biederman J, Wilens T. 2000. Pharmacothera-py of attention-deficit/hyperactivity disorder. Childand Adolescent Psychiatry Clinics of North America9(1):77–97.Swanson JM. 1991. The SNAP-IV Teacher and Parent Rat-ing Scale. Irvine, CA: University of California. Website: .Wilens TE. 1999. Straight Talk About Psychiatric Medica-tions for Kids.New York, NY: Guilford Press. Wolraich ML. 1998. Vanderbilt Teacher Behavior Evalua-tion Scale (VTBES).Nashville, TN: Vanderbilt ChildDevelopment Center. Web site: http://peds.mc./VCHWEB_1/rating~1.html.Wolraich ML, Felice ME, Drotar D, eds. 1996. The Classifi-cation of Child and Adolescent Mental Diagnoses in Pri-mary Care: Diagnostic and Statistical Manual for Primary Care (DSM-PC) Child and Adolescent Version.Elk Grove Village, IL: American Academy of Pediatrics.。

介绍一种植物的英语作文高中

介绍一种植物的英语作文高中

Lotus:BeautyThe lotus flower,a symbol of purity and elegance,stands tall among the water plants,exhibition its beauty with grace and poise.This essay aims to introduce the lotus,its unique characteristics,cultural significance,and the role it plays in our environment.Botanically speaking,the lotus belongs to the Nelumbo genus, which comprises two species:Nelumbo nucifera and Nelumbo lutea.It is a perennial aquatic plant that thrives in shallow,still,or slowly moving water bodies.The lotus leaf,with its distinctive round shape and smooth surface,floats gracefully on the water,while the stem supports the plant's elegant flower.The lotus flower,often described as"the queen of the water," blooms in a range of colors,including white,pink,red,and yellow.Its petals,arranged in a spiral pattern,unfold gracefully,revealing the lotus's delicate beauty.The flower's center is home to numerous stamens and a single pistil,surrounded by a yellow or orange disk.The lotus has a profound cultural significance in many Asian countries,particularly in China,India,and Japan.In Chinese culture,the lotus represents purity,integrity,and Spiritual enlightenment.It is often used as a symbol in poetry,paintings,and art,signifying the ideal qualities of a noble person.In Indian mythology,the lotus is associated with the goddess of beauty and love,Lakshmi,and is a symbol of prosperity and fertility.Apart from its aesthetic and cultural value,the lotus also plays a crucial role in our environment.Its leaves and stems provide habitats for various aquatic creatures,such as frogs,insects,and fish.The lotus alsohelps improve water quality by absorbing excess nutrients and pollutants.Additionally,its seeds,leaves,and flowers are used in traditional medicine and cuisine,adding to its economic value.In conclusion,the lotus flower is a remarkable plant that combines beauty,symbolism,and environmental importance.Its elegant form and profound cultural meaning make it a cherished presence in our natural world and cultural heritage.As we appreciate the lotus's beauty,we should also strive to protect and conserve its habitat,ensuring its continued existence for future generations to enjoy.。

污水中硫化亚铁和氧化铁的处理工艺流程

污水中硫化亚铁和氧化铁的处理工艺流程

污水中硫化亚铁和氧化铁的处理工艺流程In wastewater treatment, the presence of iron sulfide (FeS) and iron oxide (Fe2O3) can pose challenges. The removal of these contaminants typically involves a multi-step process that includes pre-treatment, chemical dosing, settling, and filtration.预处理阶段是必不可少的。

这个步骤通常包括物理和化学方法,以去除悬浮物、沉积物和其他杂质。

常见的预处理方法包括筛分、沉淀和调节pH值。

During the pre-treatment stage, screening is often employed to remove large solid particles from the wastewater. Sedimentation may also be utilized to allow heavier particles to settle at the bottom of the tank, facilitating their removal. Additionally, pH adjustment may be necessary to optimize subsequent treatment processes.接下来,化学投加是关键步骤之一。

根据具体情况,可以选择添加不同种类的化学试剂,以实现硫化亚铁和氧化铁的转化与沉淀。

其中常用的试剂有氢氧化钠(NaOH)、硫酸铁(FeSO4)和聚合氯化铝(PAC)等。

Chemical dosing is an essential step in the process. Depending on the specific conditions, various types of chemical agents can be added to facilitate the conversion and precipitation of iron sulfide and iron oxide. Commonly used chemicals include sodium hydroxide (NaOH), ferrous sulfate (FeSO4), and polyaluminum chloride (PAC).在投加了适量的化学试剂后,污水进入沉淀池。

句子的主要翻译方法

句子的主要翻译方法

首先是结构定位法。由于汉语里没有相应的定语结构,所以翻译时必须进行句法结构的转换。这种转换可以分为“扩展式”和“紧缩式”。
1
扩展式是根据从句对主导词的限制强弱,以主导词为中心向前后扩展,译成汉语的定语结构或独立的句子。
2
较短的(限制性和非限制性)或对主导词限制较强的,并且与其关系紧密的定语从句,通常向前扩展,译成“…的”词组作定语。如:
She had made several attempts to help them find other rental quarters without success.
It was a white wood-frame house of three creaking stories, with a black wrought-iron fire escape attached to its side like an afterthought.
1
2
合句法就是把原文中两个或两个以上的简单句,主从复合句,并列复合句,合译成一个单句。例如:
When we praise the Chinese leadership and the people, we are not merely being polite.
The little girl was very miserable. She had no money about her. All her savings had been stolen.
因此,在翻译过程中,译者必须要根据上下文和目的语行文的需要,对原句中的信息进行重新安排,调整句子重心,所以倒译法用得比较多。例如:
Generally there are two distinct philosophies on how to bring up the child so that in maturity he does not make a nuisance of himself.

汉英句子比较与翻译课件

汉英句子比较与翻译课件

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四、形合手段的综合运用
• 中国将努力促进国内粮食增产,在正常情 况下,粮食自给率不低于95%。
• China endeavors to increase its grain production so that its self-efficiency rate of grain under normal condition will be above 95 percent.
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四、肯定与否定
1.虽然是头一回拜访女友父母,张明一点都不觉得局促。 Zhang Ming was quite at his ease in spite of his first visit to his girl friend’s parents.
2.你真不够朋友,一毛钱都不给我。 Some friend you are. You won’t lead me a shilling.
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• (三)、处理方法:
• 1. 使用被动结构
• 有时候由于文化背景和风俗习惯的不同, 也容易引起误会。
• Sometimes, misunderstandings can be caused by differences in cultural backgrounds and customs.
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汉英句子成分分析
• 汉英主语、定语和状语的差异及其翻译
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• 主语:英语讲究形合,句意围绕主语展开; 汉语句子重意合,组句方式比较灵活,整 个句子一所要表达的思想为中心构建。
• (一) 、汉语主语的省略:
• 不怕寒冷,不怕危险,不怕饥饿,不怕困 难,勇敢的战士们,什么都不怕。

我国铜矿资源特征与加工,利用现状分析

我国铜矿资源特征与加工,利用现状分析

西安科技大学研究生考试试卷学号____201405197 _研究生姓名____贾建军____ 班级______ 2014 _____ 考试科目高等矿物加工工艺学考试日期________ ______ 课程学时_______ _______ 开(闭)卷________ ______题号分数阅卷人12345678910总分注意事项1、考生必须遵守考场纪律2、答题必须写清楚题号3、字迹要清楚,保持卷面整洁4、试题随试卷一起交回(试题写在黑板上时,答题时应抄写题目)我国铜矿资源特征与加工,利用现状分析贾建军(西安科技大学化学与化工学院, 西安 710000)摘要:铜是四大有色金属中较为重要的一种,被广泛的应用在国防工业、农业、机械制造、建筑材料等领域,是现代工业和科学技术必须的基础材料。

铜在自然界中主要以硫化物及其类似化合物和铜的氧化物、自然铜以及铜的硫化盐、碳酸盐、硅酸盐等类型矿物存在。

根据地质作用和矿床成因的不同可将铜矿床分为斑岩型、矽卡岩型、(火山)沉积变质型、基质—超基性铜—镍硫化物型、海相火山岩型、陆相火山岩型、海相沉积型、砂岩型、岩浆热液型九大类型。

我国铜矿资源相对贫乏,全国探明铜矿区1793个,探明铜基础储量2812万吨,主要分布于江西、内蒙古、云南、西藏、山西、安徽、甘肃、黑龙江和湖北等省份,但由于我国铜矿资源存在资源数量不少、品质不好,大矿少、小矿多,富矿少、贫矿多,便于开发利用的矿少、难以开发利用的矿多等先天禀赋,其开发利用受到一定的限制。

针对铜矿石类型的不同采用不同的选矿方法,单一硫化矿通常采用浮选法,难处理矿石会采用混合浮选法、优先浮选法或者结合重选、磁选以及湿法冶金等技术联合处理,随着矿石品位的不断降低,高效节能的选别设备、药剂开发、工艺的改进成为扩大资源利用量、提高铜精矿品位、增加矿山经济效益的重要途径。

铜矿资源的供给保障直接关系着国计民生和社会经济的可持续发展,着眼铜矿资源本身特征、资源禀赋、矿产分布以及加工利用现状的分析,对国民经济的健康发展具有十分重要的战略意义。

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Jorrrrial
of Chronralograpfay,
111 (1975)
Q Elscvier CHROM.
Scicntilic 8318
Publishing
165-l 70 Company, Amsterdam
-
Printcd
in The Netherlands
ISOLATION ALKALOIDS’
’ Paper the approv’al No. 75-03-17 from the Kentucky of the Director. Agricultural Expcrimcnt Station
and published with
1G6
L. I’. BUSH, J. A. D. JEFFREYS
PROCEDURES
Extraction of bases from the grasses was a modification of the procedure ol Mattlocks*2. Ryegrslss or tall fescue stem and leaf tissue was dried at 70” and ground to pass a 2-mm screen, A slurry of the ground grass tissue and methanol was poured into a glass column (I65 x 22 cm I.D.). By tamping the grass to remove air spaces we were able to put up to I5 kg of grass with s height of 150 cm into the glass column. Tile grass was steeped in the methanol overnight. After steeping, the methanol was percolated down through the grass and then passed through two cation exchange columns in the H+ form (Dowex 5OW-X8 or Ambe.rl.ite IR 120). The first ion-exchange column held II00 ml resin. four times the amount in the second column in tile series. From the second ion-exchange column the methanol was pumped onto the top of the grass column, thus the methanol was continuously cycled with tile bases being removed from tile methanol by the ion-exchange resin. Methanol passed through the grass column at 4-5 l/h until 15 I/kg had percolated through the grass. Methanol percolation occurred only during the daytime: therefore, tile grass was in contact with methanol for 3-5 days. When percolation with methanol was stopped. the resin column was washed with fresh methanol and then water until no colored substances were being removed. The resin was transferred to a flask and treated with an excess of base (20 g sodium carbonate in 50 ml water per 100 ml resin). The liquid was decanted and the resin
AND
SEPARATION
Байду номын сангаас
OF
TALL
FESCUE
AND
RYEGRASS
SUMMARY Bases were extractable from dried, powdered grass material by percolation with methanol. The bases were removed from the methanol by cation-exchange resins and subsequently removed from the resins. Isolation of bases by these methods eliminated the problems associated with the use of large quantities of chlorinated solvents and formation of emulsions found in previously described isolation methods. The bases were separated by paper and thin-layer chromatography (TLC). TLC and a spectrodensitonieter were used to quantify the principal alkaloids in crude extracts of tall fescue samples. This procedure recovered all of the alkaloids in spiked samples, and the standard deviation for perlolidine and perloline in tall fescue samples was 3 ‘X, or less 0r the mean value.
INTRODUCTION
peremw
The alkaloids of tall fescue (Fc~strrca cmmiimxw Schreb.) and ryegrass (Lofium L.) have been implicated in the etiology of animal diseasesle3. Alkaloids from plant tissue have been isolated by steeping or refluxing the tissue in dilute hydrochloric acid3-” or in aqueous alcol~ol~~~. Separation of the alkaloids from the crude extracts involved extraction of the alkaloids from an alkaline aqueous solution with chloroform or methylene chloride. Heavy emulsions formed at this step and were broken by centrifugation or standing For long periods of time. The emulsions and the large quantities of chlorinated solvent required for this step made this separation procedure very undesirable. Further purification of the zllkaloid fraction necessitated repetition of this step and thus enhanced the objections to this procedure. usually as perloline, was done by The quantitation of total alkaloids.
titrimctrica. colorimetric9*‘0 or gravimetric1° techniques. The titration procedure is not specific for alkaloids nor do the reagents combine with equal quantities of alkaloids, however, the quantitative estimation of total alkaloid was reported as perloline equivalents. The original calorimetric procedure9 measured absorption of total alkaloids in chloroform at 470 nm. A significant modification of this procedure was the separation of the alkaloid fraction by thin-layer chromatography (TLC) and subsequent elution of the alkaloids from the sorbent and spectrophotometric determinaHowever, many of the tall fescue and ryegrass tion of alkaloid concentration’O. alkaloids are difficult to elute from TLC sorbents or chromatographic paper and the accuracy and precision of this procedure is not satisfactory. Separation of tall fescue alkaloids into nine components by paper chromatography (PC) was reported by YateG. The paper chromatograms were equilibrated for 6-16 h and developed for 16 h with freshly prepared r7-butanol-acetic acid-water (10: I :3, v/v/v). Perloline had an RI: value of 0.46. Jeffrey@ separated ryegrass alkaloids into IO zones on Whatman No. I paper. The chromatograms were developed with ethyl acetate-acetic acid-water (75:9:9). Perloline, perlolyrine and perlolidine were found in llr ranges of 0.08-0.15. 0.50-0.60 and 0.60-0.75, respectivelyl*. Eleven alkaloid substances of tall fescue alkaloids were separated by TLC with silica gel G as the sorbcnt and developed in the upper phase of butanol-acetic acidwater (4:l :5)*O. Festucine and perloline had RI: values of 0.10 and 0.32. respectively. This TLC method was much more rapid than the PC methods and more suitable to modification for quantitative analysis of many samples. The objectives of our investigations were (I) to improve the techniques of isolating alkaloids from tall fescue and ryegrass and (2) to develop satisfactory qualitative and quantitative analytical procedures for the principal identified alkaloids.
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