欧盟电池指令问答questions_answers_directive
Recommendation 2009-1020-EU欧盟指令200533EC常见问题解答
COMMISSION RECOMMENDATIONof 21 December 2009on the safe implementation of the use of low sulphur fuel by ships at berth in Community ports(Text with EEA relevance)(2009/1020/EU)THE EUROPEAN COMMISSION,Having regard to the Treaty on the Functioning of the EuropeanUnion, and in particular Article 292 thereof,Whereas:(1) Article 4b of Council Directive 1999/32/EC of 26 April1999 relating to a reduction in the sulphur content ofcertain liquid fuels ( 1 ) as amended provides for the maximum sulphur content of marine fuels used by ships at berth in Community ports, including, as of 1 January 2010, the obligations for Member States to ensure that vessels do not use marine fuels with a sulphur content exceeding 0,1 % by mass and that marine gas oils are not placed on the market in their territory if the sulphur content of those marine gas oils exceeds 0,1 % by mass.(2) Article 6 of the Directive also provides that MemberStates shall check by sampling that the sulphur contentof marine fuels complies with the relevant provision of Article 4b and that sampling commence from the date of entry into force of the requirement.(3) As indicated in the Commission Communication onnotifications of postponements of attainment deadlinesand exemptions from the obligation to apply certain limit values pursuant to Article 22 of Directive 2008/50/EC on ambient air quality and cleaner air forEurope ( 2 ), concentrations in more than 40% of the zones and agglomerations in the Community currently exceed the daily PM 10 limit value. Implementation of low sulphur limit on fuel by ships while they are at berth in Community ports is essential to improve ambient air quality, as highlighted in the Communication from the Commission to the European Parliament and to the Council on an EU strategy to reduce atmospheric emissions from seagoing ships ( 3 ) and the Thematic Strategy on Air Pollution adopted in 2005 ( 4 ).(4) Requirements were adopted in October 2008 by theInternational Maritime Organisation (IMO) in the context of the revision of the International Convention for the Prevention of Pollution from Ships (Marpol Convention), to be implemented from 1 January 2015 for ships sailing within emission control areas as defined by Article 2(3e) of Directive 1999/32/EC.(5) The Commission, considering the safety risks at stake,deems is necessary to issue appropriate guidance to Member States in order to ensure a high level of safety and effective prevention of pollution from ships in the enforcement of the provisions of that Directive throughout the Community.(6) From 1 January 2010, ships using heavy fuel oil while atsea are to switch to lighter marine fuels such as marinediesel or gas oil when at berth in Community ports as heavy fuel oil with a sufficiently low sulphur content is not generally available.(7) There may be operational problems and safety risksassociated with the use of marine diesel and gas oil in ships that have not been designed to use such fuels or have not undergone the necessary technical adaptation. The Commission has considered the risks associated with the change of fuels and concluded that the main safety risk relates to use in ships’ boilers which have not yet been assessed and certified for use with the required type of fuel. While boilers can use heavy fuel oil or distillate fuels, a risk arises because marine diesel and gas oils are less viscous and more volatile and heating of the fuel system, which is required for heavy fuel oil, is not necessary for distillate fuels. The numbers of affected ships and the probability of such occurrences are difficult to assess precisely.(8) Directive 1999/32/EC allowed sufficient time for theshipping industry to bring about the technical adaptation to a maximum limit of 0,1 % sulphur by mass for marine fuels used by ships at berth in Community ports. Technical solutions to limit the risks are available. However, to date, there are still ships that have not gone through the necessary modifications and very few ships have undergone the necessary verification andcertification process.Journal of the European Union L 348/73( 1 ) OJ L 121, 11.5.1999, p. 13.( 2 ) COM(2008) 403. ( 3 ) COM(2002) 595. ( 4 ) COM(2005) 446.(9) Technical solutions are available to mitigate potentialconsequences of switching fuel at berth. Limiteddemand from the shipping industry has delayed thedevelopment of the necessary technical solutions,resulting in subsequent delays in the verification andcertification process.(10) The information available to the Commission underlinesthat, for these ships that have not undergone thetechnical modifications, completion of the wholeprocess should not take more than eight months.(11) There is a need for boiler and engine manufacturers todevelop specific recommendations and procedures for theretrofitting of these solutions, while shipowners shoulddevelop and implement specific operational proceduresand provide appropriate training to crews,HAS ADOPTED THIS RECOMMENDATION:1. As part of the Member States enforcement actions againstships which fail to comply with the requirement to use fuels with a maximum permitted sulphur content of 0,1 % while at berth, Member States should request those ships to provide detailed evidence of the steps they are taking to achieve compliance. This should include a contract with a manufacturer and an approved retrofit plan which should beapproved by the ship’s classification society or, for ships flying the flag of a Member State, by the organisation having recognition in accordance with Regulation (EC) No 391/2009 of the European Parliament and of the Council (1).The retrofit plan should clearly state the date of completion of the adaptation and certification process.2. Member States may consider the existence of an approvedretrofit plan when assessing the degree of penalties to be applied to non-complying ships.3. Member States should take appropriate measures to raiseawareness among owners, operators and seafarers of the safety risk related to fuel changeover in the absence of any necessary technical adaptation to a ship’s fuel system and the necessity for training to be provided.Done at Brussels, 21 December 2009.For the CommissionAntonio TAJANIVice-PresidentL 348/74 Official Journal of the European Union 29.12.2009(1) OJ L 131, 28.5.2009, p. 11.Questions and AnswersOn the use of fuel containing not more than 0.1% sulphur in ships while at berthQ: Which are the relevant articles of the Directive 1999/32/EC related to the use of 0.1% sulphur fuel at berth?A: The relevant articles are:Article 2Definitions: for the purpose of this Directive:3i. ships at berth means ships which are securely moored or anchored in a Community port while they are loading, unloading or hotelling, including the time spent when not engaged in cargo operations;Article 4bMaximum sulphur content of marine fuels used by ships at berth in Community ports1.With effect from 1 January 2010, Member States shall take all necessary measures to ensure that the following vessels do not use marine fuels with a sulphur content exceeding 0.1 % by mass:(b) ships at berth in Community ports, allowing sufficient time for the crew to complete any necessary fuel-changeover operation as soon as possible after arrival at berth and as late as possible before departure.Member States shall require the time of any fuel-changeover operation to be recorded in ships' logbooks.2.Paragraph 1 shall not apply:(a) whenever, according to published timetables, ships are due to be at berth for less than two hours;(c) until 1 January 2012 for the vessels listed in the Annex and operating exclusively within the territory of the Hellenic Republic;(d) to ships which switch off all engines and use shore-side electricity while at berth in ports.3.With effect from 1 January 2010, Member States shall ensure that marine gas oils are not placed on the market in their territory if the sulphur content of those marine gas oils exceeds 0.1 % by mass.Q: When does the requirement to use fuel not exceeding 0.1% sulphur enter into effect? Can it be postponed?A: This requirement enters into effect as of 1 January 2010 for ships visiting a Community port. The Directive does not allow for delay, nor for exemptions other than those already included and therefore it cannot be postponed.Q: Is a ship exempted in case the changeover of fuel is unsafe because the necessary modifications to the ship (or ships boiler) have not yet been implemented?A: No. The obligation for ships to use 0.1% sulphur content in fuel while at berth is the requirement of Directive 2005/33/EC (amending Directive 1999/32/EC) which was already published in 2005.The time that has been available to prepare does not justify such claim for exemption based on alleged emergency situations.Q: In which ports does the requirement to use fuel not exceeding 0.1% sulphur apply? A: This requirement applies in all Community ports, including inland ports, but excepts ports in the French oversees departments, the Azores, Madeira and the Canary Islands.Q: The ship is entering in a Community port or manoeuvring inside the port. Does this ship have the obligation to use fuel not exceeding 0.1% sulphur?A: No, this fuel requirement only applies on ships at berth, meaning securely moored or anchored in a port.Q: If a ship already has marine gas oil on board, exceeding 0.1% sulphur, can it continue using this fuel after 31 December 2009, until it needs to refuel?A: No. As of 1 January 2010 only fuel not exceeding 0.1% sulphur can be used. It is not allowed to burn non-compliant fuel, even if that fuel was bunkered before the date of entry into force.Q: At which moment does a ship has to changeover fuel?A: The requirement applies on ships at berth, meaning as from the moment when the ship is securely moored or has anchored in port. But the Directives give a margin of sufficient time for the crew to complete the necessary fuel-changeover operations as soon as possible after arrival at berth. The changeover of fuel has to be done in all engines and boilers onboard the ship which are kept running while at berth.Q: What if the ship intends to stay at berth for less than two hours?A: Only ships operating on a published timetable AND staying in a port for less than two hours are exempt. Other ships, regardless of total time foreseen to stay at berth, shall comply with the fuel obligation and start fuel-changeover when at berth, meaning as soon as possible after being securely moored at berth or at anchor in the port.Q: If a ship is anchored outside the port, does it have to use 0.1% sulphur fuel?A: No. The requirement only applies to ships at berth, meaning securely moored or anchored in a Community port.Q: What should be considered as "port" and when is a ship outside of a port?A: Directive 1999/32/EC does not contain a definition of port area. Article 11 of the UN Convention on the Law of the Sea, UNCLOS, does define ports as:For the purpose of delimiting the territorial sea, the outermost permanent harbour works which form an integral part of the harbour system are regarded as forming part of the coast.Off-shore installations and artificial islands shall not be considered as permanent harbour works.However, as the delimitations (area) of the port is established by the Competent Authority in each single Member State and not by the Directive, any further consultation should be done with the respective authorities.Q: Can LNG-carriers comply with the standard while burning a mixture of boil off gas and heavy fuel oil?A: The current text of the Directive does specify that no use of fuel containing more than 0.1% sulphur is allowed. However, as an alternative to using this low sulphur fuel, Member States may allow ships to use an approved emission abatement technology. The Commission is of the opinion that the technology to use both LNG and HFO does constitute such equivalent, provided that the mixture is such that the resulting emissions of sulphur dioxide are equal to or lower than when only burning 0.1% sulphur fuel. The Commission therefore intends to propose to Member States to allow for this equivalent. The Member States will decide on this matter in a designated Committee, which will be called together at the earliest convenience.Q: If a ship has made arrangements to install the necessary modifications to its boilers before it is able to switchover fuel safely but the modifications are not yet implemented, is it allowed to continue using HFO at berth exceeding 0.1% sulphur in the meantime? A: No, the Directive has no exemptions. However, the Commission intends to publish a Recommendation which will be aimed at the Member States and will invite them while enforcing the Directive, to request those ships which fail to comply with the Directive to provide detailed evidence of steps taken for arrangements to install the necessary modifications, including the approval by a Recognized Organization or Class. The Member States may consider the existence of an approved retrofit plan when assessing the degree of penalties to be applied to non-complying ships.Q: When does the requirement to use fuel with a sulphur content not exceeding 0.1% sulphur end?A: This requirement continues to apply while the ship is at berth or at anchor until as late as possible before departure, when it is allowed to start fuel changeover to be ready for departure.Q: Does the requirement to use fuel with a sulphur content not exceeding 0.1% still apply to a ship which has left berth or anchorage but is still sailing in the port area?A: No. The requirement does not apply to ships manoeuvring or on their way to enter or leave the port.。
欧盟废电器电子设备有关指令简介
欧盟废电器电子设备有关指令简介1. 简介欧盟废电器电子设备有关指令(WEEE Directive)是指欧盟针对电子设备的回收和处理制定的法规。
该指令旨在促进可持续发展和环境保护,确保电子设备的废物管理符合环保要求,并减少对自然资源的消耗。
2. 指令内容欧盟废电器电子设备有关指令规定了以下内容:2.1 适用范围指令适用于所有在欧盟市场上销售的电器电子设备,包括家用电器、信息技术和通信设备、娱乐设备、医疗设备、测量设备等。
无论是生产还是进口商,都需要遵守该指令。
2.2 制造商责任制造商有责任确保其生产的电器电子设备符合指令的要求。
他们需要提供与产品相关的信息,如材料组成、重量、使用说明等,并在设备上贴上符合标准的标识。
2.3 回收和处理要求指令要求各成员国建立回收和处理电器电子设备的体系。
制造商需要承担一定的费用责任,以确保设备的回收和处理得到妥善执行。
回收中心必须符合欧盟的标准要求,并负责设备的拆解和回收处理。
2.4 数据报告制造商需要向各成员国的当地管理机构提供有关销售量、回收量等数据的报告。
这些数据用于监测和评估电器电子设备废物管理的情况,并为未来政策的制定提供参考依据。
2.5 处罚和违规行为对于违反指令要求的制造商,各成员国将采取适当的处罚措施,包括罚款和禁止销售等。
这旨在强化制造商对废物管理责任的认识,增加其对环境的保护意识。
3. 实施情况和影响欧盟废电器电子设备有关指令自2003年实施以来,取得了一定的成效。
各成员国建立了废物收集和处理系统,并加强了对制造商的监管。
这些措施有助于降低环境污染、减少能源消耗,并推动可持续发展。
该指令对制造商来说也带来了一定的影响。
他们需要在产品设计和生产过程中考虑废物管理的要求,增加生产成本。
然而,通过优化废物管理和回收利用,制造商可以获得企业形象提升和节约成本的机会。
4. 未来发展与展望随着电子设备产业的快速发展和技术进步,废物管理的需求也在不断增加。
未来,欧盟废电器电子设备有关指令有望进一步完善,并且对废物管理的要求可能会更加严格。
电池指令英文(2006-66-EC)
I(Acts whose publication is obligatory)DIRECTIVE2006/66/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCILof6September2006on batteries and accumulators and waste batteries and accumulators and repealing Directive91/157/EEC(Text with EEA relevance)THE EUROPEAN PARLIAMENT AND THE COUNCIL OF THE EURO-PEAN UNION,Having regard to the Treaty establishing the European Com-munity,and in particular Article175(1)thereof and Article95(1)thereof in relation to Articles4,6and21of this Directive,Having regard to the proposal from the Commission(1),Having regard to the opinion of the European Economic and Social Committee(2),Having regard to the opinion of the Committee of Regions(3),Acting in accordance with the procedure laid down in Article251of the Treaty(4),in the light of the joint text approved by the Conciliation Committee on22June2006,Whereas:(1)It is desirable to harmonise national measuresconcerning batteries and accumulators and wastebatteries and accumulators.The primary objective of thisDirective is to minimise the negative impact of batteriesand accumulators and waste batteries and accumulatorson the environment,thus contributing to the protection,preservation and improvement of the quality of theenvironment.The legal base is therefore Article175(1)of the Treaty.However,it is also appropriate to takemeasures at Community level on the basis ofArticle95(1)of the Treaty to harmonise requirementsconcerning the heavy metal content and labelling ofbatteries and accumulators and so to ensure the smoothfunctioning of the internal market and avoid distortionof competition within the Community.(2)The Commission Communication of30July1996onthe Review of the Community Strategy for WasteManagement established guidelines for future Com-munity waste policy.That Communication stresses theneed to reduce the quantities of hazardous substances inwaste and points out the potential benefits of Com-munity-wide rules limiting the presence of suchsubstances in products and in production processes.Itfurther states that,where the generation of waste cannotbe avoided,that waste should be reused or recovered forits material or energy.(3)The Council Resolution of25January1988on a Com-munity action programme to combat environmentalpollution by cadmium(5)stressed the limitation of theuses of cadmium to cases where suitable alternatives donot exist and the collection and recycling of batteriescontaining cadmium as major elements of the strategyfor cadmium control in the interests of the protection ofhuman health and the environment.(4)Council Directive91/157/EEC of18March1991onbatteries and accumulators containing certain dangeroussubstances(6)has brought about an approximation ofMember States'laws in this field.However,the objectivesof that Directive have not been fully attained.DecisionNo1600/2002/EC of the European Parliament and ofthe Council of22July2002laying down the Sixth Com-munity Environment Action Programme(7)and Direc-tive2002/96/EC of the European Parliament and of theCouncil of27January2003on waste electrical and elec-tronic equipment(WEEE)(8)also underlined the need forDirective91/157/EEC to be revised.Directive91/157/EEC should therefore be revised and replaced inthe interests of clarity.(1)OJ C96,21.4.2004,p.29.(2)OJ C117,30.4.2004,p.5.(3)OJ C121,30.4.2004,p.35.(4)Opinion of the European Parliament of20April2004(OJ C104E,30.4.2004,p.354),Council Common Position of18July2005(OJC264E,25.10.2005,p.1)and Position of the European Parliament of13December2005(not yet published in the Official Journal).(5)OJ C30,4.2.1988,p.1.(6)OJ L78,26.3.1991,p.38.Directive as amended by CommissionDirective98/101/EC(OJ L1,5.1.1999,p.1).(7)OJ L242,10.9.2002,p.1.(5)In order to achieve its environmental aims,this Directiveprohibits the placing on the market of certain batteriesand accumulators containing mercury or cadmium.Italso promotes a high level of collection and recycling ofwaste batteries and accumulators and improved environ-mental performance of all operators involved in the lifecycle of batteries and accumulators, e.g.producers,distributors and end-users and,in particular,thoseoperators directly involved in the treatment and recy-cling of waste batteries and accumulators.The specificrules needed to do this are supplementary to existingCommunity legislation on waste,in particular Direc-tive2006/12/EC of the European Parliament and of theCouncil of5April2006on waste(1),Council Direc-tive1999/31/EC of26April1999on the landfill ofwaste(2)and Directive2000/76/EC of theEuropean Parliament and of the Council of4December2000on the incineration of waste(3).(6)In order to prevent waste batteries and accumulatorsfrom being discarded in such a way as to pollute theenvironment,and to avoid end-user confusion about thedifferent waste management requirements for differentbatteries and accumulators,this Directive should applyto all batteries and accumulators placed on the marketwithin the Community.Such a wide scope should alsoensure economies of scale in collection and recycling,aswell as optimal resource saving.(7)Reliable batteries and accumulators are fundamental forthe safety of many products,appliances and services,and are an essential energy source in our society.(8)It is appropriate to distinguish between portable batteriesand accumulators on the one hand and industrial andautomotive batteries and accumulators on the other.Thedisposal of industrial and automotive batteries and accu-mulators in landfill sites or by incineration should beprohibited.(9)Examples of industrial batteries and accumulatorsinclude batteries and accumulators used for emergencyor back-up power supply in hospitals,airports or offices,batteries and accumulators used in trains or aircraft andbatteries and accumulators used on offshore oil rigs orin lighthouses.Examples also include batteries and accu-mulators designed exclusively for hand-held paymentterminals in shops and restaurants,bar code readers inshops,professional video equipment for TV channelsand professional studios,miners'lamps and diving lampsattached to mining and diving helmets for professionals,back up batteries and accumulators for electric doors toprevent them from blocking or crushing people,batteries and accumulators used for instrumentation orin various types of measurement and instrumentationequipment and batteries and accumulators used inconnection with solar panel,photo-voltaic,and otherrenewable energy applications.Industrial batteries andaccumulators also include batteries and accumulatorsused in electrical vehicles,such as electric cars,wheel-chairs,bicycles,airport vehicles and automatic transportvehicles.In addition to this non exhaustive list of exam-ples,any battery or accumulator that is not sealed andnot automotive should be considered industrial.(10)Examples of portable batteries and accumulators,whichare all-sealed batteries and accumulators that an averageperson could carry by hand without difficulty and thatare neither automotive batteries or accumulators norindustrial batteries or accumulators,include single cellbatteries(such as AA and AAA batteries)and batteriesand accumulators used by consumers or professionals inmobile telephones,portable computers,cordless powertools,toys and household appliances such as electrictoothbrushes,razors and hand-held vacuum cleaners(including similar equipment used in schools,shops,restaurants,airports,offices or hospitals)and any batteryor accumulator that consumers may use for normalhousehold applications.(11)The Commission should evaluate the need for adaptationof this Directive,taking account of available technicaland scientific evidence.In particular,the Commissionshould carry out a review of the exemption from thecadmium ban provided for portable batteries and accu-mulators intended for use in cordless power tools.Exam-ples of cordless power tools are tools that consumersand professionals use for turning,milling,sanding,grinding,sawing,cutting,shearing,drilling,makingholes,punching,hammering,riveting,screwing,polishing or similar processing of wood,metal and othermaterials,as well as for mowing,cutting and othergardening activities.(12)The Commission should also monitor,and MemberStates should encourage,technological developmentsthat improve the environmental performance of batteriesand accumulators throughout their entire life cycle,including through participation in a Community eco-management and audit scheme(EMAS).(13)In order to protect the environment,waste batteries andaccumulators should be collected.For portable batteriesand accumulators,collection schemes achieving a highcollection rate should be established.This means settingup collection schemes so that end-users can discard allwaste portable batteries and accumulators conveniently(1)OJ L114,27.4.2006,p.9.(2)OJ L182,16.7.1999,p.1.Directive as amended by Regulation(EC)(14)It is desirable for Member States to achieve a high collec-tion and recycling rate for waste batteries and accumula-tors so as to achieve a high level of environmentalprotection and material recovery throughout the Com-munity.This Directive should therefore set minimumcollection and recycling targets for Member States.It isappropriate to calculate the collection rate on the basisof average annual sales in preceding years,so as to havecomparable targets for all Member States that areproportionate to the national level of battery and accu-mulator consumption.(15)Specific recycling requirements should be established forcadmium and lead batteries and accumulators in orderto attain a high level of material recovery throughoutthe Community and to prevent disparities betweenMember States.(16)All interested parties should be able to participate incollection,treatment and recycling schemes.Thoseschemes should be designed to avoid discriminationagainst imported batteries and accumulators,barriers totrade or distortions of competition.(17)Collection and recycling schemes should be optimised,in particular in order to minimise costs and the negativeenvironmental impact of transport.Treatment and recy-cling schemes should use best available techniques,asdefined in Article2(11)of Council Directive96/61/ECof24September1996concerning integrated pollutionprevention and control(1).The definition of recyclingshould exclude energy recovery.The concept of energyrecovery is defined in other Community instruments.(18)Batteries and accumulators can be collected individually,by way of national battery collection schemes ortogether with waste electrical and electronic equipment,by way of national collection schemes set up on thebasis of Directive2002/96/EC.In the latter case,as anobligatory minimum treatment requirement,batteriesand accumulators should be removed from the collectedwaste electrical and electronic equipment.After theirremoval from the waste electrical and electronic equip-ment,batteries and accumulators are subject to therequirements of this Directive,notably they count forachieving the collection target and are subject to recy-cling requirements.(19)Basic principles for financing the management of wastebatteries and accumulators should be set at Communitylevel.Financing schemes should help to achieve highcollection and recycling rates and to give effect to theprinciple of producer responsibility.All producers asdefined by this Directive should be registered.Producersshould finance the costs of collecting,treating and recy-cling all collected batteries and accumulators minus theprofit made by selling the materials recovered.However,under certain circumstances,the application of deminimis rules to small producers could be justified.(20)The provision of information to end-users on the desir-ability of separate collection,the collection schemesavailable and end-users'role in the management of wastebatteries and accumulators is necessary for successfulcollection.Detailed arrangements should be made for alabelling system,which should provide end-users withtransparent,reliable and clear information on batteriesand accumulators and any heavy metals they contain.(21)If,in order to achieve the objectives of this Directive,and,in particular,to achieve high separate collectionand recycling rates,Member States use economic instru-ments,such as differential tax rates,they should informthe Commission accordingly.(22)Reliable and comparable data on the quantities ofbatteries and accumulators placed on the marketcollected and recycled are necessary for monitoringwhether the objectives of this Directive have beenachieved.(23)Member States should lay down rules on the penaltiesapplicable to infringements of the provisions of thisDirective and ensure that they are implemented.Thosepenalties should be effective,proportionate and dissua-sive.(24)In accordance with paragraph34of the Interinstitutionalagreement on better law-making(2),Member States areencouraged to draw up,for themselves and in the inter-ests of the Community,their own tables,which will,asfar as possible,illustrate the correlation between thisDirective and the transposition measures and to makethem public.(25)The measures necessary for the implementation of thisDirective should be adopted in accordance with CouncilDecision1999/468/EC of28June1999laying downthe procedures for the exercise of implementing powersconferred on the Commission(3).(26)Since the objectives of this Directive namely protectingthe environment and ensuring the proper functioning ofthe internal market cannot be sufficiently achieved bythe Member States and can therefore,by reason of thescale or effects of the action,be better achieved at Com-munity level,the Community may adopt measures,inaccordance with the principle of subsidiarity as set outin Article5of the Treaty.In accordance with the prin-ciple of proportionality,as set out in that Article,thisDirective does not go beyond what is necessary in orderto achieve those objectives.(27)This Directive applies without prejudice to Communitylegislation on safety,quality and health requirements andspecific Community waste management legislation,inparticular Directive2000/53/EC of the European Parlia-ment and of the Council of18September2000on end-of-life vehicles(1)and Directive2002/96/EC.(28)As regards producer responsibility,producers of batteriesand accumulators and producers of other productsincorporating a battery or accumulator are responsiblefor the waste management of batteries and accumulatorsthat they place on the market.A flexible approach isappropriate to enable financing schemes to reflectdiffering national circumstances and to take account ofexisting schemes,particularly those set up to complywith Directives2000/53/EC and2002/96/EC,whileavoiding double charging.(29)Directive2002/95/EC of the European Parliament and ofthe Council of27January2003on the restriction of theuse of certain hazardous substances in electrical andelectronic equipment(2)does not apply to batteries andaccumulators used in electrical and electronic equip-ment.(30)Automotive and industrial batteries and accumulatorsused in vehicles should meet the requirements of Direc-tive2000/53/EC,in particular Article4thereof.There-fore the use of cadmium in industrial batteries and accu-mulators for electrical vehicles should be prohibited,unless they can benefit from an exemption on the basisof Annex II to that Directive,HAVE ADOPTED THIS DIRECTIVE:Article1Subject-matterThis Directive establishes:(1)rules regarding the placing on the market of batteries andaccumulators and,in particular,a prohibition on the placing on the market of batteries and accumulators containing hazardous substances;and(2)specific rules for the collection,treatment,recycling anddisposal of waste batteries and accumulators to supplement relevant Community legislation on waste and to promote a high level of collection and recycling of waste batteries and accumulators.It seeks to improve the environmental performance of batteries and accumulators and of the activities of all economic opera-tors involved in the life cycle of batteries and accumulators,e.g.producers,distributors and end-users and,in particular, those operators directly involved in the treatment and recycling of waste batteries and accumulators.Article2Scope1.This Directive shall apply to all types of batteries and accumulators,regardless of their shape,volume,weight,mate-rial composition or use.It shall apply without prejudice to Directives2000/53/EC and2002/96/EC.2.This Directive shall not apply to batteries and accumula-tors used in:(a)equipment connected with the protection of MemberStates'essential security interests,arms,munitions and war material,with the exclusion of products that are not intended for specifically military purposes;(b)equipment designed to be sent into space.Article3DefinitionsFor the purposes of this Directive,the following definitions shall apply:(1)‘battery’or‘accumulator’means any source of electricalenergy generated by direct conversion of chemical energy and consisting of one or more primary battery cells(non-rechargeable)or consisting of one or more secondary battery cells(rechargeable);(2)‘battery pack’means any set of batteries or accumulatorsthat are connected together and/or encapsulated within an outer casing so as to form a complete unit that the end-user is not intended to split up or open;(3)‘portable battery or accumulator’means any battery,button cell,battery pack or accumulator that:(a)is sealed;and(b)can be hand-carried;and(c)is neither an industrial battery or accumulator nor anautomotive battery or accumulator;(4)‘button cell’means any small round portable battery oraccumulator whose diameter is greater than its height and which is used for special purposes such as hearing aids, watches,small portable equipment and back-up power;(1)OJ L269,21.10.2000,p.34.Directive as last amended by Council(6)‘industrial battery or accumulator’means any battery oraccumulator designed for exclusively industrial or profes-sional uses or used in any type of electric vehicle;(7)‘waste battery or accumulator’means any battery or accu-mulator which is waste within the meaning of Article1(1)(a)of Directive2006/12/EC;(8)‘recycling’means the reprocessing in a production processof waste materials for their original purpose or for other purposes,but excluding energy recovery;(9)‘disposal’means any of the applicable operations providedfor in Annex IIA to Directive2006/12/EC;(10)‘treatment’means any activity carried out on wastebatteries and accumulators after they have been handed over to a facility for sorting,preparation for recycling or preparation for disposal;(11)‘appliance’means any electrical or electronic equipment,as defined by Directive2002/96/EC,which is fully or partly powered by batteries or accumulators or is capable of being so;(12)‘producer’means any person in a Member State that,irre-spective of the selling technique used,including by means of distance communication as defined in Directive97/7/ EC of the European Parliament and of the Council of 20May1997on the protection of consumers in respect of distance contracts(1),places batteries or accumulators, including those incorporated into appliances or vehicles, on the market for the first time within the territory of that Member State on a professional basis;(13)‘distributor’means any person that provides batteries andaccumulators on a professional basis to an end-user;(14)‘placing on the market’means supplying or making avail-able,whether in return for payment or free of charge,to a third party within the Community and includes import into the customs territory of the Community;(15)‘economic operators’means any producer,distributor,collector,recycler or other treatment operator;(16)‘cordless power tool’means any hand held appliancepowered by a battery or accumulator and intended for maintenance,construction or gardening activities;(17)‘collection rate’means,for a given Member State in agiven calendar year,the percentage obtained by dividing the weight of waste portable batteries and accumulators collected in accordance with Article8(1)of this Directive or with Directive2002/96/EC in that calendar year by the average weight of portable batteries and accumulators that producers either sell directly to end-users or deliver to third parties in order to sell them to end-users in that Member State during that calendar year and the preceding two calendar years.Article4Prohibitions1.Without prejudice to Directive2000/53/EC,Member States shall prohibit the placing on the market of:(a)all batteries or accumulators,whether or not incorporatedinto appliances,that contain more than0,0005%of mercury by weight;and(b)portable batteries or accumulators,including those incorpo-rated into appliances,that contain more than0,002%of cadmium by weight.2.The prohibition set out in paragraph1(a)shall not apply to button cells with a mercury content of no more than2%by weight.3.The prohibition set out in paragraph1(b)shall not apply to portable batteries and accumulators intended for use in: (a)emergency and alarm systems,including emergencylighting;(b)medical equipment;or(c)cordless power tools.4.The Commission shall review the exemption referred to in paragraph3(c)and submit a report to the European Parlia-ment and to the Council by26September2010,together,if appropriate,with relevant proposals,with a view to the prohi-bition of cadmium in batteries and accumulators.Article5Increased environmental performanceMember States which have manufacturers established on their territory shall promote research and encourage improvements in the overall environmental performance of batteries and accu-mulators throughout their entire life cycle as well as the devel-opment and marketing of batteries and accumulators which contain smaller quantities of dangerous substances or which contain less polluting substances,in particular as substitutes for mercury,cadmium and lead.Article6Placing on the market1.Member States shall not,on the grounds dealt with in this Directive,impede,prohibit,or restrict the placing on the market in their territory of batteries and accumulators that meet the requirements of this Directive.2.Member States shall take the necessary measures toArticle7Overarching objectiveMember States shall,having regard to the environmental impact of transport,take necessary measures to maximise the separate collection of waste batteries and accumulators and to minimise the disposal of batteries and accumulators as mixed municipal waste in order to achieve a high level of recycling for all waste batteries and accumulators.Article8Collection schemes1.Member States shall ensure that appropriate collection schemes are in place for waste portable batteries and accumula-tors.Such schemes:(a)shall enable end-users to discard waste portable batteries oraccumulators at an accessible collection point in their vici-nity,having regard to population density;(b)shall require distributors to take back waste portablebatteries or accumulators at no charge when supplying portable batteries or accumulators,unless an assessment shows that alternative existing schemes are at least as effec-tive in attaining the environmental aims of this Directive.Member States shall make public such assessments;(c)shall not involve any charge to end-users when discardingwaste portable batteries or accumulators,nor any obliga-tion to buy a new battery or accumulator;(d)may be run in conjunction with the schemes referred to inArticle5(2)of Directive2002/96/EC.Collection points set up to comply with point(a)of this para-graph shall not be subject to the registration or permit require-ments of Directive2006/12/EC or Council Directive91/689/ EEC of12December1991on hazardous waste(1).2.Provided that the schemes meet the criteria listed in para-graph1,Member States may:(a)require producers to set up such schemes;(b)require other economic operators to participate in suchschemes;(c)maintain existing schemes.3.Member States shall ensure that producers of industrial batteries and accumulators,or third parties acting on their behalf,shall not refuse to take back waste industrial batteries and accumulators from end-users,regardless of chemical composition and origin.Independent third parties may also collect industrial batteries and accumulators.4.Member States shall ensure that producers of automotive batteries and accumulators,or third parties,set up schemes for the collection of waste automotive batteries and accumulators from end-users or from an accessible collection point in their vicinity,where collection is not carried out under the schemes referred to in Article5(1)of Directive2000/53/EC.In the case of automotive batteries and accumulators from private,non-commercial vehicles,such schemes shall not involve any charge to end-users when discarding waste batteries or accumulators, nor any obligation to buy a new battery or accumulator.Article9Economic instrumentsMember States may use economic instruments to promote the collection of waste batteries and accumulators or to promote the use of batteries and accumulators containing less polluting substances,for instance by adopting differential tax rates.If they do so,they shall notify the measures related to the imple-mentation of those instruments to the Commission.Article10Collection targets1.Member States shall calculate the collection rate for the first time in respect of the fifth full calendar year following the entry into force of this Directive.Without prejudice to Directive2002/96/EC,annual collection and sales figures shall include batteries and accumulators incor-porated into appliances.2.Member States shall achieve the following minimum collection rates:(a)25%by26September2012;(b)45%by26September2016.3.Member States shall monitor collection rates on a yearly basis according to the scheme set out in Annex I.Without prejudice to Regulation(EC)No2150/2002of the European Parliament and of the Council of25November2002on waste statistics(2),Member States shall transmit reports to the Commission within six months of the end of the calendar year concerned.Reports shall indicate how they obtained the data necessary to calculate the collection rate.4.In accordance with the procedure referred to in Article24(2):(a)transitional arrangements may be laid down to addressdifficulties faced by a Member State in satisfying the requirements of paragraph2as a result of specific national circumstances;。
20041125欧盟电子电气设备环保指令对策研讨会——企业交流问题解答
1、应对DVD专利纠纷,中国电子音响工业协会(CAIA)作为国内DVD企业的代表与国际专利权人谈判,而企业不必单独谈判,只需加入CAIA即可。
那么应对WEEE指令是否也可以如此?国家或行业协会组织一个统一的回收系统,各企业只要加入即可处理自身报废的电子产品。
我们期望能这样。
答:就现时我们掌握的资料,基本欧盟大部分成员都有自身已经在运作的回收体系,所以根据出口到具体国家的情况,出口商加入其回收体系应该是没问题的,只是每个国家的运作方式有所不同,那么涉及每种产品的回收费用略有不同。
详细信息建议参考(1)《欧盟系列环保指令指南-基础知识篇》第二章内容;(2)我中心网站“焦点关注”中“weee—rohs”专栏中“欧洲报废电子电气设备指令(WEEE)在欧盟各国法律转换的报告(英文)”2004年9月份版本。
其中详细介绍了各国现有的回收体系情况,以及有些国家回收的费用预测。
我们将推出的《欧盟系列环保指令指南-对策参考篇》也将纳入最新情况。
敬请留意。
2、关于RoHS指令中提到的“同质材料”,现在仍无一个确定的定义,请问企业应该怎么应对?答:请留意VIC CLEMENT先生的讲课内容。
另外现时的定义我们倾向于参考英国DTI贸工部的《final consultation paper on the WEEE and RoHS directives》(截至日期为10月29日)。
英国的转换法规草案已涉及此内容,且预计改变的可能性很小。
也可在我中心网站上查询。
3、如何降低绿色壁垒应对的成本。
答:总体来说实施“环境化/生态设计”—从产品的研发阶段开始考虑将受限制的各种环境因素。
但是具体实施因公司各种情况千差万别,所以很难一概而论。
建议留意郭财吉教授的讲课,另外我中心将推出的《欧盟系列环保指令指南-对策参考篇》也将纳入有关实施“环境化/生态设计”的缘由,案例,国外操作等内容。
4、具体化电子产品豁免的范围?答:具体请参见WEEE和RoHS指令原文。
欧盟关于电池相关指令汇集——中英文
Whereas provision should be made for consumer information in this field;
鉴于确定对于在告知消费者分开收集和循环使用的信息的规定。
Whereas provision should be made for appropriate procedures to implement the provisions of this Directive, particularly the making system, and to ensure that the Directive can be easily adapted to scientific and technical progress; whereas the committee referred to in Article 18 of Directive 75/442/EEC should be instructed to assist the Commission in these tasks,
欧盟电池指令(91/157/EC)
Council Directive 91/157/EEC of 18 March 1991 on batteries and accumulators containing certain dangerous substances
1991年3月18日委员会《关于电池和蓄电池含某些危险物质的指令(91/157/EEC)》
whereas the Commission should be informed of these programmes and of the specific measures taken;
欧盟废电器电子设备有关指令(WEEE)(RoHS) 简介及要点介绍
22
電機電子環境發展協會
绿色供应链建构与管理实例
成为GP member的条件与步骤: 一、供货商负责人同意接受工厂审查,并遵照
S公司标准生产交货: SS-00259
(在部件和设备中含有限制使用物质的管理标准)
23
電機電子環境發展協會
绿色供应链建构与管理实例
成为GP member的条件与步骤: 二、实地审查:
PBB
17
可能衝擊的產品與製程 電路板上之零件如晶片電阻、連接材料、表面處理、低 熔點焊接、保險絲、鹼性電池化學合成材料、馬達、開 關、繼電器、漏電開閉器等的電氣接點材料、半導體受 光元件 、油漆、墨水、螢光管等。 電機電子設備、焊接、塗蠟材料、電氣連接、鉛酸電池 、 橡膠固化劑、CRT、顏料、玻璃、塗料、橡膠硫化促進 劑、固體潤滑劑等。 溫度計、感應器、開關、繼電器、醫療器材、金屬蝕刻、 乾電池、防腐劑、電極、水銀燈、電訊設備、手機等 顏料、催化劑、電鍍、墨水、陶瓷用著色劑、防腐劑、 相片等。 熱溶劑、潤滑劑和電容器油等。
印刷電路板、連接器、電線、塑膠外殼上之耐燃劑。
電機電子環境發展協會
肆、台商及产业之因应及具体做法
绿色产品的设计 绿色供应链的建构与运营
─合格供货商的选择、管理与评审
绿色采购政策推行 清洁生产的规划、执行、监督与
持续改善
18
電機電子環境發展協會
肆、台商及产业之因应及具体做法
一、成立或指定专责机构研读并密切掌握相关贸 易地区和各国对WEEE、RoHS等指令的实施
2.易拆卸之组装设计
3.减少用料的设计
4.节约能源的设计
20
電機電子環境發展協會
涵盖产品生命周期的绿色设计活动
市场营销 企划 研究开发
与欧洲电池指令对应的英国法规
与欧洲电池指令对应的英国法规英国对欧洲电池指令的法规引言:欧洲电池指令旨在确保电池的安全性和环境友好性,对欧洲市场上销售的电池制定了一系列规定。
作为欧盟成员国之一,英国在脱欧之后仍然受到欧洲电池指令的约束。
本文将探讨英国对欧洲电池指令的法规,包括电池标签和标识、回收和处理、市场监管等方面的规定。
一、电池标签和标识为了保护消费者的权益和提供准确的信息,英国制定了一系列关于电池标签和标识的法规。
根据欧洲电池指令,电池应该标注有关键信息,包括电池类型、电压、容量、化学成分等。
英国进一步规定,销售电池的商家必须确保电池标签和标识清晰可见,以便消费者正确识别和使用。
二、回收和处理电池的回收和处理是欧洲电池指令的核心要求之一。
英国制定了一系列规定,确保电池在使用寿命结束后可以有效回收和安全处理。
根据英国法规,电池制造商和销售商有责任建立回收和处理电池的系统,并提供便利的回收点。
此外,英国还规定了不同类型电池的回收和处理方式,以确保其环境友好性。
三、市场监管为了确保电池市场的公平竞争和产品质量的安全可靠,英国对电池市场进行了严格的监管。
根据英国法规,电池制造商和销售商必须遵守产品安全要求,并对产品进行合格性评估。
此外,英国还设立了专门的机构来监管电池市场,对不符合要求的电池进行检测和处罚。
四、电池的禁用和限制为了保护公众的健康和环境,英国对某些有害物质在电池中的使用进行了禁用和限制。
根据英国法规,镉、铅和汞等有毒物质的含量应该控制在特定的限制值以下。
此外,英国还对含有这些有害物质的电池进行了禁止销售的规定,以确保公众的安全。
五、处罚和违规处理对于违反欧洲电池指令和英国相关法规的企业和个人,英国设立了相应的处罚措施。
根据英国法规,违规者可能面临罚款、产品召回、市场禁售等处罚。
此外,英国还鼓励公众积极举报违规行为,以加强市场监管和保护消费者权益。
结论:英国作为欧盟成员国,对欧洲电池指令的法规进行了有效的贯彻和执行。
FAQ_WEEE_ROHS-chinese&english
_____________________________________________________________________________________________________ TÜV Product Service Ltd. Question and AnswersQuestion and Answersregarding the Directives2002/96/ECon waste electrical and electronic equipment (WEEE)and2002/95/ECon the restriction of the use of certain hazardoussubstances in electrical and electronic equipment (RoHS)关于废弃电子电气设备2002/96/EC 指令(WEEE)以及限制有害物质在电子电气设备中使用2002/95/EC 指令 (RoHS)的问与答_____________________________________________________________________________________________________ TÜV Product Service Ltd. Question and AnswersQ: Has the RoHS effective date changed? I thought it was July 1, 2006? 问: RoHS 的生效日期是否更改了?我以为是2006年7月1日。
A: The RoHS Directive (2002/95/EC) entered into force on the day of its publication in the OJ (February 13, 2003). Member States of the EU are requested to bring into force the laws, regulations and administrative provisions to comply with this Directive before August 13, 2004. From July 1, 2006 new electrical and electronic equipment put on the market shall not contain the six hazardous substances listed in the RoHS Directive.答: RoHS 指令(2002/95/EC) 从它在官方的定期刊物(Official Journal)上公布的那天(2003年2月13日)开始强制使用。
欧盟电池环保指令 EU BattEry DirEctivE 200666Ec
the EU’s 2006/66/Ec, a landmark for eco-friendly batteriesBattery products contain pollutants such as lead, cadmium, mercury, acids and alkali, which can be released into the environment when discarded improperly. considering their widespread use, their eventual disposal poses an eminent threat to the ecosystem and the health of people. to counter this, countries have established and implemented strict measures to limit the amount of hazardous substances found in batteries. Linked to battery recycling and reuse initiatives, these have successfully reduced environmental impacts and pushed manufacturers to reconsider the end of life part of their product cycle.tÜv rheinland’s testing services ensure that the batteries you produce or include in your products comply with the EU’s 2006/66/Ec battery directive – the highest standard in the market. Batteries that meet this norm demonstrate conformity with legally accepted thresholds of hazardous substances and match the precise quantified content targets for collection and recycling. Our experts can help harmonise safety and accountability of your batteries through proper labelling that lists provisions for disposal and demonstrates producer responsibility. We contribute to making uninterrupted power supply cleaner.2006/66/EC,电池环保风向标由于电池产品含铅、镉、汞、酸、碱等污染物质,当其任意丢弃在环境中,有害物质就会慢慢溢出,直接或间接对生态环境和人类健康造成严重危害,因此,越来越多的国家制定和实施相关措施限制电池中的有害物质。
欧盟ROHS指令培训资料
第二章:讨论RoHS指令
令中,“均质物质”的定义作了解释:“(均质物质就是用
机械方法拆分到不能再拆分的最小单元a unit that cannot be mechanically disjoined into single materials)”但 是,在业界,对于这个定义产生了多种的理解,因此,需要 对均质物质的正确定义作出正确的阐述。 ▪ 制造商们被允许在产品中使用多少有害物质在于被禁用的物 质是应用在单一物质,不连续的装置或者材料的集合元件中。
最终用户的电子电气废弃物; IV. 2006年6月30日,RoHS指令的六种有害物质将被禁用; V. 2006年12月31日,各成员国应保证达到回收目标 VI.2008年2月13日,欧盟委员会就指令的实施情况做正式报告,
并且会对指令作必要的修改; VII. 2008年12月31日,对实施效果重新评估,建立新的收
❖ 过量镉堆积在肾脏,则会造成肾小管损伤,而衍生肾衰竭。 根据临床研究,镉本身也是一种致癌物质,其亦可以引起[肺 癌]
❖ 镉的半衰期可以长达三十多年,很不幸的截至目前为止,[镉 中毒]并没有特效的解药。
第一章: 初步认识
❖ 重金属 – 铅(Pb)
❖法规要求:89/677EEC,2002/95/EC ❖测试方法:US EPA 3050B ❖限值:400PPM(欧盟1000) ❖特殊应用:油漆、涂料、设备所使用之电池/蓄
电气产品(除去第八项医疗设备和第九项显 示和控制仪器),此外,对于大型固定的工 业设备也在豁免之列。
欧盟电池新指令 -回复
欧盟电池新指令-回复什么是欧盟电池新指令?欧盟电池新指令是指欧洲联盟在2020年通过的一项立法,旨在统一和规范欧盟成员国内的电池市场,并提高欧盟范围内电池产品的质量、安全性和环保性能。
这一指令将取代之前的欧盟电池指令,以适应不断发展的电动汽车和可再生能源行业。
为什么需要电池新指令?随着电动汽车的迅速发展和可再生能源的推广,电池产品在欧盟市场中的需求不断增加。
然而,由于各个成员国对电池的规定和标准存在差异,导致电池市场的不规范和不公平竞争现象。
此外,一些低质量和不安全的电池产品的存在也给消费者带来了安全隐患。
因此,欧盟电池新指令的出台旨在解决这些问题,并提供一个更加规范和安全的电池市场。
欧盟电池新指令的主要内容是什么?欧盟电池新指令的主要内容包括以下几个方面:1. 电池的分类:新指令将电池分为可重复充电电池和一次性电池两类,根据其不同的特性和用途制定相应的标准和要求。
2. 材料和制造要求:电池制造商必须符合一系列的材料和制造要求,确保其产品的质量和安全性。
3. 标签和包装要求:电池产品必须在标签上清楚地显示其类型、容量、能量密度等相关信息,以便消费者能够准确选择和使用。
4. 回收与再利用:为了促进电池的可持续发展,新指令要求电池制造商设立回收和再利用机制,确保废弃电池的安全处理和资源回收。
5. 进口和市场监管:新指令强调了对进口电池产品的监管和检查,确保市场上的电池产品符合相关标准和要求。
欧盟电池新指令的实施对谁有影响?欧盟电池新指令的实施对相关行业和利益相关者有重要的影响。
1. 电池制造商:欧盟电池新指令将会给电池制造商带来更加严格的标准和要求,需要他们不断提高产品的质量和安全性,以满足欧盟市场的需求。
2. 消费者:欧盟电池新指令的实施将保证消费者能够购买到符合标准和安全要求的电池产品,增加他们对电池产品的信心。
3. 环境保护:通过强调电池的回收与再利用,欧盟电池新指令有助于减少废弃电池对环境的污染,并促进资源的可持续利用。
2006_66_EC, 电池新法案-2013_56_EU常见问题
Commission Services document - not legally binding
Foreword This Frequently Asked Questions (FAQ) document on Directive 2006/66/EC on batteries and accumulators and waste batteries and accumulators updates and replaces an earlier version of the document. It takes account of a number of amendments to the Directive including those agreed under Directive 2013/56/EU, which entered into force on 30 December 2013 and which Member States are required to transpose into national law by 1 July 2015 The document is principally intended to help competent public authorities and economic operators interpret the provisions of the Directive in order to ensure compliance with the Directive’s requirements. However, the Directive being addressed only to the Member States, the rights and obligations for private parties exclusively flow from the measures enacted by the authorities of the Member States to implement it. This FAQ document is considered to be a ‘living document’ and the Commission may update it as necessary in light of the experience with the implementation of the Directive and any future requirements. Finally, as is customary, this FAQ document reflects the views of DG Environment and as such is not legally binding. Binding interpretation of EU legislation is the exclusive competence of the Court of Justice of the European Union.
欧盟汽车动力电池指令及相关要求
欧盟汽车动力电池指令及相关要求对于电池的监管,欧盟设立了电池指令、ROHS指令、WEEE指令、REACH法规等多重技术性贸易壁垒。
3.1. 电池指令2006/66/EC欧盟新电池和蓄电池指令2006/66/EC于2008年9月26日生效,同时废止原有的电池指令(91/157/EEC)及其修订条文(98/101/EC和93/86/EEC,并要求各成员国必须于2008年9月26日前将新电池指令转化为本国法例。
该指令适用于所有类型的电池和蓄电池,不管其形状、容量、质量、组成材料或使用的情况是怎样均在新电池指令的规定范围之中。
当然,指令不适用于与保护成员国特殊安全利益有关的设备,武器、军需品、战争用品等设备中的电池和预计要送入太空的设备中的电池。
对于并非特定用于军事的设备中电池不算在豁免清单里面。
3.1.1 电池分类管理在新的电池指令中,电池被分为了四类:便携式电池(Portable batteries)、钮扣电池(button battery)、工业电池(Industrial battery)和汽车电池(Automotive battery)。
工业电池(Industrial battery)是指仅用于工业或专业用途或用于任何类型的电动车辆的电池或蓄电池,如铅-酸电池、镍-镉电池,锂离子电池。
汽车电池(Automotive battery)是指任何用于汽车的启动器、照明或点火电源的电池或蓄电池;如用于启动、照明和汽车点火的铅-酸电池。
该指令明确了电池组、便携电池、汽车电池和工业电池等的要求。
主要体现在以下几个方面:▪修改对电池中汞和镉使用限制的规定;▪提出电池标签的新要求,为消费者的选购和回收提供明确提示;▪修改铅、汞和镉含量的标签标识;▪废弃便携电池的回收率目标;▪禁止对工业用和汽车用废弃电池进行掩埋和焚化;▪增加“生产商责任”的规定;▪电池必须可以从宿主产品上取除(由于安全、性能、医疗或数据完整性原因必须永久连接电池的除外);▪从2009年9月26日起,便携式、汽车电池应在标签上注明容量。
欧盟电池新指令 -回复
欧盟电池新指令-回复关于欧盟电池新指令引言:欧盟一直致力于推进环境保护和可持续发展。
随着电动汽车和可再生能源的快速发展,电池已经成为欧盟重要的能源储存和使用方式。
然而,电池的生产和处理也带来了一系列环境和健康问题。
为了规范电池的生产、回收和处理过程,欧盟在2019年颁布了一项新的电池指令。
本文将就欧盟电池新指令进行一步一步的解析。
第一部分:指令背景和目标1.1 指令的背景和原因电池作为一种常用的能源储存设备,在欧盟各成员国有着广泛的应用。
然而,电池的生产和处理过程中产生的废弃物对环境和人类健康构成了潜在威胁。
此外,电池的原材料有限,提高电池的可持续性也成为了当务之急。
1.2 指令的目标和意义欧盟电池新指令的目标在于保护环境和人体健康,并提高电池的可持续性。
通过对电池的生产、回收和处理过程进行规范,欧盟希望减少电池相关的污染,并促进电池材料的回收和再利用。
第二部分:关键要点和规范内容2.1 电池生产环节的规范欧盟电池新指令从电池生产的角度对相关要求进行了明确规定。
例如,指令对电池中有害物质的使用进行限制,如铅、汞、镉等。
此外,指令还要求生产商在产品上标识重金属的含量,并提供相关的安全警示标志。
2.2 电池回收和处理规范电池回收和处理是欧盟电池新指令的重要内容之一。
指令要求成员国建立电池回收系统和处理中心,并制定相应的回收和处理标准。
此外,生产商也有责任参与电池的回收和处理,并为此支付相关费用。
2.3 电池可持续性的提升为了提高电池的可持续性,欧盟电池新指令还对电池材料的再利用和资源回收进行了规范。
指令鼓励电池制造商使用可再生材料,并要求对回收的电池材料进行再利用。
此外,指令还要求成员国制定相应的循环经济政策,促进电池材料的再循环利用。
第三部分:指令的实施和挑战3.1 指令的实施进展自2019年发布以来,欧盟成员国已经开始着手落实电池新指令。
一些国家已经建立了相应的电池回收和处理系统,并对电池生产商进行了相关审查和监管。
欧盟电池新指令 -回复
欧盟电池新指令-回复欧盟电池新指令:推动可持续发展的能源存储解决方案引言:电池作为能源存储的关键技术在当今社会扮演着至关重要的角色。
为了推动可持续发展,欧洲联盟(EU)制定了一项新的电池指令。
这一指令为电池行业提供了一系列新的规定和要求,旨在推动经济、环境和社会可持续性。
本文将从可持续能源的重要性、电池产业现状、欧盟电池新指令的背景和内容,以及影响和挑战等方面逐步展开,来详细探讨这一重要的话题。
第一部分:可持续能源的重要性在人类持续发展的过程中,能源存储的重要性日益凸显。
可再生能源是未来的发展方向,如太阳能和风能等。
然而,由于可再生能源的间断性和不可控性,电池等储能技术变得至关重要。
这也是为什么推动可持续发展以及开展电池产业研究和发展变得至关重要的原因。
第二部分:电池产业现状目前,电池市场正在快速增长。
锂离子电池是广泛应用于电动汽车和可再生能源系统的主导技术。
尽管这些电池在可再生能源存储中具有巨大的潜力,但同时也存在一些问题。
例如,电池的使用寿命短、资源消耗多、回收困难等。
这些问题需要得到解决,以推动电池技术的进一步发展。
第三部分:欧盟电池新指令的背景和内容为了解决电池产业面临的挑战并推进可持续发展,欧盟制定了一项新的电池指令。
这一指令旨在确保电池的生命周期内可追踪和可持续的生产、使用和回收。
指令要求电池制造商提供详细的信息,包括材料来源、生产过程和能量效率等。
此外,该指令还将规范回收利用率、环境标签、产品标识等方面的规定,以确保电池的可持续性和消费者权益。
第四部分:影响和挑战欧盟电池新指令的实施将对电池产业和相关领域产生广泛的影响。
首先,电池制造商需要全面改进其生产和供应链流程,以满足指令中的要求。
这可能需要额外的投资和技术改革。
其次,电池回收和再利用的要求将提高回收产业的需求。
这将刺激相关的产业发展,并为欧洲的可持续发展做出贡献。
然而,这也将面临监管和技术挑战,包括如何确保电池的有效回收和安全处理。
关于欧盟RoHS指令与电池指令解读
关于欧盟RoHS指令与电池指令解读欧盟RoHS指令与电池指令解读王金良欧盟RoHS指令从2021年7月1日起开始实施。
RoHS指令的主要内容有哪些?企业如何应对?怎样进行RoHS符合性评价?电池生产商还应执行哪些相关指令?上下游产品标准不一致时到底按哪个标准执行?应业内骨干厂家和部分技术人员的要求,王金良先生对欧盟RoHS指令及与电池相关的环保指令作如下解读,并对其间的相互关系作了分析。
现转发给各会员单位,请认真学习和及早采取相应的措施。
1 目前涉及电池和蓄电池的欧盟环保指令(主要指令,包括未来可能执行的指令) 1.1 电子电气设备中限制使用某些有害物质指令2002/95/EC,简称RoHS指令; 1.2 报废电子电气设备指令2002/96/EC简称WEEE指令; 1.3 废旧车辆报废指令2000/53/EC ;1.4 包装及包装废弃物指令――94/62/EC指令及其延展指令2021/12/EC;1.5 含某些有毒物质的电池和蓄电池指令91/157/EEC、延展指令98/101/EC,简称电池指令; 1.6 含某些有毒物质的电池和蓄电池指令修改草案EEC 98号通报;1.7 欧盟未来化学品政策:化学品的注册、评估、授权和限制,简称REACH法规。
2 RoHS指令和WEEE指令(目前已执行的主要环保指令) 2.1 RoHS指令2002/95/ECRoHS指令是电子电气设备中限制使用某些有害物质指令( The Restriction of the Use of Certain Hazardous Substances in Electrical and Electronic Equipment)的简称。
编号为2002/95/EC。
核心内容: 2021年7月1日起,新投放欧盟市场的电子电气设备中6种有害物质的最高限量(w%)分别为:铅(Pb):0.1%;汞(Hg):0.1%;镉(Cd):0.01%;六价铬(Cr):0.1%;多溴联苯(PBB):0.1% ;多溴二苯醚(PBDE):0.1%。
与欧洲电池指令对应的英国法规
与欧洲电池指令对应的英国法规英国法规:电池和蓄电池指令引言:欧洲电池指令(Battery Directive)于2006年通过,旨在减少电池和蓄电池对环境和人类健康的影响。
作为欧盟成员国,英国在实施欧洲电池指令的同时也制定了相应的法规,即电池和蓄电池指令(Battery and Accumulator Regulations)。
本文将重点介绍这些规定,并解释其对英国市场和消费者的影响。
一、指令概述电池和蓄电池指令是为了控制电池和蓄电池在生产、销售和处置过程中的环境影响而制定的。
它要求生产商和销售商在产品上提供相关信息,以便消费者能够正确使用和处置电池和蓄电池。
二、指令内容1. 标识要求根据电池和蓄电池指令,生产商和销售商需要在电池和蓄电池上标识相关信息,包括化学成分、重金属含量、容量、生产日期等。
这些信息旨在帮助消费者了解产品特性和环境影响,并正确使用和处置电池和蓄电池。
2. 回收要求电池和蓄电池指令要求生产商和销售商提供回收和处理电池和蓄电池的机制。
他们需要建立回收网络,确保消费者能够方便地回收废旧电池和蓄电池,以减少对环境的污染。
3. 限制重金属含量电池和蓄电池指令限制了电池和蓄电池中重金属的含量,如汞、铅和镉等。
这是为了减少这些有害物质对环境和人类健康的影响。
生产商和销售商需要确保其产品符合这些限制要求。
4. 生产商责任电池和蓄电池指令规定了生产商的责任。
他们需要确保其产品符合相关要求,并承担相应的责任,如提供正确的标识、信息和回收机制。
如果产品未符合要求或引发环境问题,生产商需要承担相应的法律责任。
三、对英国市场和消费者的影响1. 产品合规性电池和蓄电池指令对生产商和销售商提出了严格的要求,以确保产品符合相关标准和限制要求。
这有助于提高市场中电池和蓄电池产品的质量和安全性,保障消费者的权益。
2. 消费者权益保护电池和蓄电池指令要求在产品上提供详细的标识和信息,使消费者能够了解产品的特性、性能和环境影响。
欧盟电池新指令
欧盟电池新指令2022年6月15日,欧盟发布了新的电池指令,旨在推动欧洲电动汽车和可再生能源产业的发展,提高电池的可持续性和环保性能。
这一指令对于全球电池行业的发展起到了重要的推动作用,也为中国电池企业提供了新的机遇和挑战。
新指令要求电池的可充电性能、安全性、环保性等方面都要达到更高的标准。
首先,电池必须具备更高的能量密度和更长的续航里程,以满足市场对电动汽车的需求。
同时,电池的安全性要得到更好的保障,防止发生火灾、爆炸等事故。
此外,电池的材料必须尽量避免使用有害物质,以减少对环境的污染,并且要实现高效的回收利用。
为了实现这些要求,欧盟提出了一系列具体措施。
首先,欧盟将加大对电池研发和生产的支持力度,鼓励企业投入更多的资金和资源。
同时,欧盟还将加强对电池行业的监管,加强对电池产品和生产过程的质量控制。
此外,欧盟还将建立电池回收体系,推动电池的资源循环利用。
这一新指令对中国电池企业而言既是机遇又是挑战。
中国是全球最大的电池生产国,拥有丰富的电池产业基础和技术优势。
新指令的发布将为中国电池企业提供更大的市场需求和研发合作的机会,助力企业向高端产业链迈进。
然而,新指令提出的更高标准也对中国电池企业提出了更高的要求,必须加大科技创新投入,提升产品和生产工艺的质量水平,以适应欧盟市场的需求。
中国电池企业可以借鉴欧盟的经验和做法,积极响应新指令,提升产品质量和安全性能。
企业需要加强技术研发,提高电池的能量密度和续航里程,以满足市场对电动汽车的需求。
同时,企业还需加大环保投入,探索绿色、可再生的电池材料,并建立高效的回收体系,实现电池资源的循环利用。
总之,欧盟的新电池指令为全球电池行业的可持续发展指明了方向。
中国电池企业应积极应对,提升产品的质量和环保性能,加大科技创新投入,开展国际合作,以适应新形势下的市场需求。
只有这样,才能在全球电池竞争中立于不败之地,为行业的可持续发展做出贡献。
欧盟电池法的豁免
欧盟电池法的豁免欧盟电池法(EU Battery Directive)是欧盟制定的关于电池回收和处理的法规。
该法规规定了对于消费电池的回收和处理要求,目的是保护环境和人类健康。
然而,在某些特定情况下,根据欧盟电池法的规定,某些电池可以获得豁免,不需要遵守该法规的要求。
首先,根据欧盟电池法的规定,电池的种类可以影响是否获得豁免。
一些电池,比如可再充电电池(如镍氢电池和锂离子电池)以及铅酸电池,在特定的条件下可以获得豁免。
这是由于这些电池的回收和处理成本较高,同时它们在使用过程中对环境和人类健康的影响也较小。
因此,欧盟电池法对这些电池规定了一些灵活的豁免规定。
其次,欧盟电池法还规定了一些其他情况下可以获得豁免的情况。
例如,对于一些特殊用途的电池,比如军事用电池或航空用电池,根据欧盟电池法的规定,可以获得豁免。
这是因为这些电池的回收和处理过程可能与一般消费电池存在差异,且这些电池的使用情况也可能与普通消费电池存在较大的不同。
另外,欧盟电池法还对诸如动力电池等其他特定类型的电池制定了豁免规定。
动力电池主要用于电动车等交通工具中,其回收和处理过程的复杂性较高。
根据欧盟电池法的规定,对于这些特定类型的电池,可以获得一定的豁免。
这也是为了保证电动交通工具的发展和推广,以减少对环境的污染。
总体而言,欧盟电池法的豁免规定是为了充分考虑电池的种类和用途的特殊性,并确保环境和人类健康的保护的同时,为相关行业和技术的发展提供灵活性。
这些豁免规定确保了在特定情况下,不需要对所有电池都严格进行回收和处理的要求,以降低相关成本并促进相关行业的健康发展。
然而,值得注意的是,欧盟电池法的豁免规定并不意味着可以任意忽视电池的回收和处理。
即使获得豁免,相关企业和组织仍然需要遵守其他环境保护和法律法规的要求,确保电池的合理使用、回收和处理,以减少对环境和人类健康的影响。
总而言之,欧盟电池法的豁免规定为特定类型的电池在回收和处理方面提供了一定的灵活性。
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Q UESTIONS AND A NSWERSON THEB ATTERIES D IRECTIVE (2006/66/EC)TABLE OF CONTENTS1. A NEW BATTERIES DIRECTIVE – A NEW SCOPE (4)Why did we need a new Directive on batteries? (4)What is the scope of the Batteries Directive 2006/66/EC? (4)Why does Directive 2006/66/EC apply to all batteries and not just to hazardous ones? (4)2. CONTENT OF DIRECTIVE 2006/66/EC (5)2.1. Objective (5)What is the objective of the Directive? (5)What are the environmental problems addressed by the Directive? (5)How are these environmental problems addressed? (5)What is the internal market problem addressed? (6)How is this internal market problem addressed? (6)2.2. Preventive measures (6)What are the preventive measures in the Directive? (6)2.3. Collection (7)What are the proposed battery collection requirements? (7)What are the proposed collection targets? (7)Why is there no collection target for industrial and automotive batteries? (7)2.4. Recycling (8)Why should we recycle batteries? (8)What examples are there for energy savings related to the use of recycledmetals in batteries? (8)What are the recycling requirements in the Directive? (8)What are the recycling efficiencies in the Directive? (8)Are there any requirements for the treatment of waste batteries in the Directive? (9)2.5. Financing/producer responsibility (9)Who will pay for the collection, treatment and recycling of batteries? (9)What is the definition of "battery producer"? (9)Who is the "battery producer"? - Examples (9)How does the Batteries Directive deal with small producers? (10)How does the Batteries Directive deal with the "free rider" problem on thebatteries market? (10)2.6. Labels/End-user information (10)What labelling requirements apply to batteries? (10)How will end-users know what to do with the waste batteries? (11)Who is responsible for informing the public? (11)2.7. Removability of batteries from appliances (11)What requirement does the Directive contain regarding the removal of waste batteries from appliances? (11)What does "batteries and accumulators can be readily removed" mean? (11)When should waste batteries and accumulators be removable from appliances? (12)2.8. Export of waste batteries (12)What requirements need to be fulfilled if batteries are exported for recycling? (12)2.9. Implementation of the Directive (12)How long do Member States have to transpose the requirements of this Directive? (12)What is the legislation that batteries placed on the EU market and batterymanufacturers/producers must comply with before and after 26September 2008? (12)Can Member States transpose the provisions of Directive 2006/66/EC intotheir national law now? (13)Can the Directive be transposed on the basis of environmental agreementswith industry? (13)By when do collection targets for portable batteries have to be met? (13)When do the recycling requirements enter into force? (13)Are Member States encouraged to use economic instruments to implementthe Directive? (13)3. SUMMARY OF THE MEASURES IN THE DIRECTIVE ACCORDING TOBATTERY TYPE (13)What are the different types of batteries? (13)Do batteries used for agricultural purposes qualify as industrial batteries? (14)Are batteries used in hybrid vehicles (vehicles that run on a combination offuel and electricity) automotive or industrial batteries? (14)Which batteries are the most harmful? (15)What specific measures apply to portable batteries and accumulators? (15)What specific measures apply to industrial batteries? (15)What specific measures apply to automotive batteries in the Directive? (16)4. LINK WITH OTHER PIECES OF LEGISLATION (16)What is the relationship between the Batteries Directive and the ELV Directive? (16)What is the relationship between the Batteries Directive and the RoHS/WEEE Directives? (17)Does the RoHS or the Batteries Directive apply to the outer casings of battery packs? (17)What is the relationship between the Batteries Directive and IPP ? (18)What is the relationship between the Batteries Directive and the ThematicStrategy on Sustainable use of Resources? (18)What is the relationship between the Batteries Directive and the RecyclingStrategy? (18)1.A NEW B ATTERIES D IRECTIVE – A NEW SCOPEWhy did we need a new Directive on batteries?Previous Community legislation on batteries (Directive 91/157/EEC) has failed to adequately control the risks posed by batteries in the waste stream and to create a homogeneous framework for battery collection and recycling.For example, in 2002, approximately 45.5 % of the total amount of portable batteries sold in the EU-15 (i.e. 72 155 tonnes) went for final disposal, i.e. landfilling/incineration.1 Also, many spent batteries, which were collected, were disposed of instead of being recycled.2Moreover, a homogeneous framework for battery collection and recycling was needed, in particular as regards financing, in order to avoid free-riders on the market and to create a level playing-field for all the actors involved.What is the scope of the Batteries Directive 2006/66/EC?The Directive applies to all batteries and accumulators placed on the Community market. In line with Article 2(3) of the WEEE Directive,3 batteries and accumulators used in equipment connected with the protection of the essential security interests of the Member States are excluded from the scope of this Directive. Also, equipment designed to be sent into space does not fall under the scope of the Directive.Why does Directive 2006/66/EC apply to all batteries and not just to hazardous ones?Directive 2006/66/EC applies to all batteries because:–all batteries contain substances which are more or less harmful to the environment;–experience with the previous Directive (91/157/EEC) on hazardous batteries (batteries containing mercury, cadmium or lead)4showed that ‘all battery’ collection schemes are more efficient than separate schemes for certain types of portable batteries;5–all batteries contain metals which are recyclable,6so the collection and recycling of all batteries help save resources in conformity with Article 174 of the EC Treaty.1 Extended Impact Assessment by the European Commission SEC (2003)1343, p.112Extended Impact Assessment by the European Commission SEC (2003)1343, p.123 Directive 2002/96/EC on waste electrical and electronic equipment (WEEE)4Commission Decision 2000/532/EC5 Extended Impact Assessment by the European Commission SEC (2003)1343, p.192.C ONTENT OF D IRECTIVE 2006/66/EC2.1.ObjectiveWhat is the objective of the Directive?The objective of the Directive is twofold:1. To contribute to a high level of environmental protection2. To contribute to the proper functioning of the internal market.What are the environmental problems7 addressed by the Directive?There are a number of environmental concerns which arise when dealing with the waste management of batteries and accumulators. These relate for the most part to the metals contained in these batteries.Mercury, lead and cadmium are by far the most problematic substances in the battery waste stream. Lead batteries, Ni-Cd batteries and mercury containing batteries are classified as hazardous waste by Commission Decision 2000/532/EC.Other metals commonly used in batteries, such as zinc, copper, manganese, lithium and nickel, may also constitute environmental hazards.When batteries are incinerated, the metals used in them contribute to air emissions and pollute incineration residues. When batteries end up in landfills, the metals can contribute to the leachate from landfills. Moreover, on a resource management level, batteries are considered as a source of secondary raw materials. Thousands of tonnes of metals, including valuable metals such as nickel, cobalt and silver, can be recovered if batteries are recycled.How are these environmental problems addressed?The Directive aims to avoid the final disposal of batteries and accumulators by enhancing their collection and recycling. The Directive also contains restrictions on the substances used in batteries and accumulators.The Directive establishes:–restrictions on the use of mercury in all batteries and restriction on the use of cadmium in portable batteries with certain exemptions;–collection requirements for all batteries, as well as collection targets for portable batteries; –the requirement that all batteries and accumulators collected must undergo sound treatment and recycling (with possible exemptions for portable hazardous batteries);– a ban on the landfilling/incinerating of automotive and industrial batteries;–the requirement that battery recycling processes must meet minimum recycling efficiencies.What is the internal market problem addressed?Many national battery collection and recycling schemes do not operate efficiently and have not been able to benefit from the internal market. There has been no clear framework for the functioning of these schemes, which has led to different applications of the producer responsibility principle at Member State level and diverging marketing requirements.How is this internal market problem addressed?The Directive harmonises product requirements for batteries:–it restricts the use of mercury in all batteries and of cadmium in portable batteries, with certain exceptions;–it establishes labelling requirements for batteries: (i) chemical symbols Hg, Pb or Cd, (ii) crossed-out wheel bin and (iii) capacity labelling.The Directive states that Member States cannot prohibit the placing on the market of batteries that meet the requirements of this Directive.In addition to this the Directive lays down minimum rules for the functioning of national battery collection and recycling schemes, in particular with respect to the financing of these schemes by producers. In order to avoid free-riders, Member States should keep a register of producers who place batteries on the national market.2.2.Preventive measuresWhat are the preventive measures in the Directive?The Directive restricts the use of mercury in all batteries.Furthermore, the Directive restricts the use of cadmium in portable batteries with a list of exemptions (batteries intended for use in emergency and alarm systems, including emergency lighting, medical devices and cordless power tools).In addition to this, Member States are required to promote research and encourage improvements in the environmental performance of batteries through their life-cycle and encourage the marketing of batteries which contain less polluting substances (in particular substitutes for mercury, cadmium and lead).What are the proposed battery collection requirements?The Batteries Directive aims at as much collection of spent batteries and accumulators (portable, industrial and automotive) as possible. To this end it specifies the following collection requirements:–Consumers should be able to bring back portable batteries to collection points in their vicinity, free-of-charge and without obligation to buy a new battery;–Distributors should take back waste portable batteries when supplying portable batteries (unless it is proven that the existing alternative schemes are as effective);–Producers of industrial batteries, or third parties acting on their behalf, are obliged to take industrial batteries back from end-users;–Producers of automotive batteries, or third parties, should set up collection schemes for waste automotive batteries not collected through collection schemes set up under the Directive on end-of-life vehicles (ELV Directive).8 For waste automotive batteries from non-commercial vehicles, these schemes should be free-of-charge for end-users and without obligation to buy a new battery.What are the proposed collection targets?The Batteries Directive establishes an overall collection target for all spent portable batteries of 25% to be achieved by 2012 and 45% by 2016.Why is there no collection target for industrial and automotive batteries?The combination of the legal obligations on the take-back of these batteries and accumulators and the ban on landfilling and incineration aims to ensure the collection of these batteries.Unlike spent portable batteries and accumulators, spent industrial and automotive batteries are less likely to be disposed of in the municipal solid waste stream (a) because they are large and (b) because their users are professionals and are likely to appreciate the economic value of recycling.With current practice, the collection of industrial and automotive batteries is already close to 100%:–lead-acid batteries are collected because of the value of recycled lead;–nickel-cadmium batteries are collected because there is a well-developed collection system in place.8Directive 2000/53/ECWhy should we recycle batteries?Battery recycling helps to save resources by allowing for the recovery of valuable metals such as nickel, cobalt and silver.9The use of recycled metals in batteries requires less energy consumption.10What examples are there for energy savings related to the use of recycled metals in batteries? Using recycled cadmium and nickel requires respectively 46% and 75% less primary energy than the extraction and refining of virgin metals.For zinc, the ratio of the energy needed for recycling to the energy needed for extraction of primary resources is of the order of 2.2 to 8.11What are the recycling requirements in the Directive?All batteries collected should be recycled.However, with respect to waste portable batteries containing mercury, cadmium or lead, Member States may put them in landfills or underground storage in two cases:–when this is part of a national strategy to phase out heavy metals and an impact assessment shows that landfill/underground storage is a better option than recycling; or–when no viable end-market is available.In addition to the requirement to recycle all batteries collected, the Directive also specifies recycling efficiency levels focusing on the quality of the recycling process.What are the recycling efficiencies in the Directive?Battery recycling processes have to meet the following recycling efficiencies by September 2011:–Lead-acid batteries: recycle lead as far as technically feasible, and recycle a minimum of 65% of batteries by average weight;–Nickel-cadmium batteries: recycle cadmium as far as technically feasible, and recycle a minimum of 75% of batteries by average weight;–Other batteries: recycle a minimum of 50% of batteries by average weight.9 Extended Impact Assessment by the European Commission SEC (2003)1343, p.1310 Extended Impact Assessment by the European Commission SEC (2003)1343, p.13Are there any requirements for the treatment of waste batteries in the Directive?In addition to the recycling efficiencies, the Directive also specifies treatment requirements, the minimum being removal of fluids and acids. Conditions for treatment and storage are also described.2.5.Financing/producer responsibilityWho will pay for the collection, treatment and recycling of batteries?In line with the producer responsibility principle, battery producers have to finance the cost of the collection, treatment and recycling of waste batteries. Producers and users of industrial and automotive batteries may conclude agreements stipulating alternative financial arrangements (Art. 16(5)). Producers are also responsible for financing the costs of public information campaigns on the collection, treatment and recycling of waste portable batteries. Member States must make sure there is no double-charging of producers where batteries are collected under Directive 2000/53/EC on end-of life vehicles and Directive 2002/96/EC on waste electrical and electronic equipment.What is the definition of "battery producer"?According to the definition in Article 3 of the Directive, the ‘producer’ is the person in a Member State who supplies or makes available to a third party batteries or accumulators (including those incorporated into appliances or vehicles) within the territory of that Member State for the first time on a professional basis. This definition applies irrespective of the selling technique used and irrespective of whether the batteries are made available in return for payment or free of charge. This includes import into the customs territory of the Community.Who is the "battery producer"? - Examples− A battery manufacturer or a domestic importer sells batteries to a retailer who in turn sells them to end-users in the same Member StateIn this case, the battery manufacturer or the domestic importer is the producer in that Member State, as they are the ones placing the batteries on the market for the first time.− A retailer sells batteries in a Member State; the batteries were bought outside that Member StateA retailer sells batteries to end-users in a given Member State which he bought in anothercountry. In this case, as the retailer is placing these batteries on the market for the first time in the given Member State, the retailer is the producer.−An equipment/car manufacturer buys batteries within a Member State; these batteries are then sold together with the equipment/car in the same Member StateA battery manufacturer or domestic importer in a Member State sells batteries to anequipment or car manufacturer in the same Member State who will then put the battery into equipment or a car and sell it on the market of this Member State. In this case, thebattery manufacturer or domestic importer is the producer in this Member State as they are placing the batteries on the market for the first time.− A car/equipment manufacturer buys batteries outside a Member State, then incorporates them into equipment/a car and sells this in the Member StateThe car/equipment manufacturer or domestic importer sells cars/equipment in a given Member State with batteries incorporated. The batteries for the car/equipment were bought outside this Member State. Since in this case it is the equipment or car manufacturer or domestic importer who places these batteries on the market of the Member State for the first time, they are the battery producers in this Member State.− A company imports batteries from a non-EU parent company for its independent subsidiary located in a Member StateIn this case the independent European subsidiary is the producer, as it is the subsidiary which places the batteries on the market in that Member State.−Batteries or battery cells are sold in a Member State to a battery pack assembler and are then sold within the same Member StateIn this case the battery pack assembler is the producer, as it makes the battery pack available on the market for the first time on a professional basis within the territory of the Member State.How does the Batteries Directive deal with small producers?The Batteries Directive allows Member States to exempt small producers from the financial producer responsibility obligations on the condition that this does not impede the proper functioning of the battery collection and recycling schemes.The Batteries Directive also provides for harmonisation of the procedural requirements for producer registration among Member States, on the basis of a comitology procedure. A harmonised system will reduce the administrative burden of registration.How does the Batteries Directive deal with the "free rider" problem on the batteries market? Member States must keep a national register of all battery producers/importers. The procedural requirements for registration will be harmonised on the basis of a comitology procedure.bels/End-user informationWhat labelling requirements apply to batteries?–Crossed-out wheeled bin applies to all batteries;–Chemical symbols (Hg, Cd, Pb), indicating the heavy metal content of batteries, apply to batteries containing more than a given amount of these substances;–Portable and automotive batteries must be labelled with a capacity label after 26 September 2009.How will end-users know what to do with the waste batteries?The Directive includes obligations to inform end users of:–the potential environmental and health effects of substances used in batteries;–the desirability of not disposing of batteries as municipal waste, but collecting them separately;–the collection and recycling schemes available;–consumers' role in contributing to the recycling of waste batteries;–the meaning of labels.Who is responsible for informing the public?Member States must ensure that the public is informed. Battery producers are responsible for financing public information campaigns on collection, treatment and recycling of waste portable batteries. Economic operators may be required to provide end-users with information on the issues mentioned under the previous question.2.7.Removability of batteries from appliancesWhat requirement does the Directive contain regarding the removal of waste batteries from appliances?Article 11 of Directive 2006/66/EC requires that ‘manufacturers design appliances in such a way that waste batteries and accumulators can be readily removed’ and that ‘appliances into which batteries and accumulators are incorporated shall be accompanied by instructions showing how they can be removed safely’.Exemptions to these requirements are allowed for appliances where, for safety, performance, medical or data integrity reasons, continuity of power supply is necessary and requires a permanent connection between the appliance and the battery or accumulator.What does "batteries and accumulators can be readily removed" mean?End-users or professionals (e.g. appliance service centres, waste treatment facilities) should be able to remove batteries from appliances. The instructions showing how the batteries can be readily and safely removed should also specify who, in the view of the manufacturer, is the best person to safely remove the battery.The instructions should also describe any dangers of not complying with the battery removal instructions.Where there is more specific legislation applying to specific products (e.g. toys) on how the batteries should be removed, these products should comply with those specific rules.When should waste batteries and accumulators be removable from appliances?Waste batteries should be removable from the appliances during the lifetime of the appliance if the batteries normally have a shorter lifetime than the appliance, or at the latest at the end of the life of the equipment, as applicable.2.8.Export of waste batteriesWhat requirements need to be fulfilled if batteries are exported for recycling?When waste batteries are sent for recycling to another Member State or exported for recycling outside the Community, they must comply with waste shipment laws as specified in Article 15 of the Batteries Directive, noting that as Regulation No 259/93 was repealed on 12 July 2007, the transfer of the waste should comply with the new Regulation No 1013/2006 on shipments of waste.12When waste batteries are exported outside the Community, Member States should ensure that sound evidence is provided that the recycling operations taking place outside the Community meet equivalent conditions as set out in this Directive, including those on recycling efficiencies by 2011.2.9.Implementation of the DirectiveHow long do Member States have to transpose the requirements of this Directive?Member States have until 26 September 2008 to transpose the requirements of this Directive. What is the legislation that batteries placed on the EU market and battery manufacturers/producers must comply with before and after 26 September 2008?Batteries placed on the European Union market and battery manufacturers/producers have to comply with the national legislation transposing Directive 91/157/EEC until 25 September 2008. Batteries placed on the EU market and battery manufacturers/producers will have to comply with national legislation transposing Directive 2006/66/EC from 26 September 2008. However, in order to ensure better protection for the environment, the Commission encourages battery manufacturers/producers to comply with the requirements of the new Batteries Directive as soon as possible.12Especially Article 49 of Regulation 1013/2006 should be considered.Can Member States transpose the provisions of Directive 2006/66/EC into their national law now?Yes. Member States can already transpose the requirements of Directive 2006/66/EC. This transposition must be finalised by 26 September 2008 at the latest. However, the transposed national legislation shall only take effect from 26 September 2008.Can the Directive be transposed on the basis of environmental agreements with industry?Yes. Member States can conclude environmental agreements with economic operators to transpose provisions on the collection of waste batteries, the export of waste batteries, and information for end-users.By when do collection targets for portable batteries have to be met?The collection target for portable batteries of 25% has to be met by 26 September 2012. Experience in those Member States that have developed collection schemes has shown that collection schemes need 4 to 5 years to become efficient, so this gives Member States with underdeveloped collection schemes sufficient time to set up efficient battery collection schemes.The higher collection target of 45% should be achieved by 26 September 2016.When do the recycling requirements enter into force?–By 26 September 2009 all batteries collected should be recycled (with Member States having the possibility to landfill/store portable hazardous batteries under certain conditions);–By 26 September 2011 battery recycling processes should meet minimum recycling efficiencies of 65% (for lead-acid batteries), 75% (for nickel-cadmium batteries) and 50% (for other batteries) with the best lead and cadmium recycling possible.Are Member States encouraged to use economic instruments to implement the Directive?Yes. The Directive specifies that Member States can use economic instruments to promote the collection of waste batteries and the use of batteries containing less polluting substances.3.S UMMARY OF THE MEASURES IN THE DIRECTIVE ACCORDING TO BATTERY TYPEWhat are the different types of batteries?The Directive distinguishes between three battery types: portable batteries, industrial batteries and automotive batteries.–Portable batteries:Portable batteries are batteries that are sealed, can be hand-carried and are neither industrial nor automotive batteries.They can be:–non-rechargeable batteries (e.g. zinc-carbon and alkaline manganese - ‘general purpose batteries’), button cells, and lithium-oxide batteries; together these represent around 75% of the portable battery segment;13–Rechargeable batteries (e.g. nickel-cadmium, nickel metal hydride, lithium-ion and lead-acid batteries), which represent about 25% of the portable battery segment.–Industrial batteries:Industrial batteries are batteries that are designed for exclusively industrial or professional uses or used in any type of electric vehicles.Industrial batteries are for example14:–lead-acid batteries (96% of the total industrial battery segment);–NiCd batteries (2% of the total industrial battery segment).–others (2%)–Automotive batteries:Batteries used for vehicle starting, lighting and ignition.Do batteries used for agricultural purposes qualify as industrial batteries?According to Article 3 of the Directive, industrial batteries are defined as batteries designed for exclusively industrial or professional uses or used in any kind of electric vehicle. If the agricultural equipment concerned is designed for exclusively professional agricultural use, its battery is an industrial battery.Are batteries used in hybrid vehicles (vehicles that run on a combination of fuel and electricity) automotive or industrial batteries?There is a battery in hybrid vehicles that is used as an automotive starter for lighting and for ignition power. This is generally a 12 V battery (usually lead-acid battery). This battery is an automotive battery.There is another type of battery in hybrid cars used mainly for propulsion purposes and as a warm starter in (Lithium ion or a Nickel Metal Hydride battery). As this battery does not have 13 Bio Intelligence Final report of July 2003, p. 814Extended Impact Assessment by the European Commission SEC (2003)1343, p.65。