EN 2003-02-EC Arsenic 0

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2003版企标冷轧产品相近牌号对照表(国内外)

2003版企标冷轧产品相近牌号对照表(国内外)

B340/590DPE+ZN



B400/780DPE+Z



B400/780DPE+ZN



B340LAE+Z


H340LA
B340LAE+ZN


B410LAE+Z B410LAE+ZN
JEC590R -
- JNC590R
H420LA
标准号
彩涂产品相近牌号对照表
Q/BQB
JIS
440-2003

65A1300

65A1600
ASTM A677M-99
- - 47F280 - - 47F400 47F450 - - 64F320 - - 64F550 - -
EN 10106-1996
- - M470-50A M530-50A M600-50A M700-50A M800-50A - - M600-65A M700-65A M800-65A - - -
SECD

JEC 270D
DX2
DS
DC03+ZN
JNC 270D

DC04+ZE
SECE

JEC 270E
DX3
DDS

DC04+ZN

JNC 270E


DC05+ZE -
- DC05+ZN


JEC 270F

EDDS

JNC 270F


BSUFDE+Z DC06+ZE

EN及EPA等系列标准 中文名称

EN及EPA等系列标准 中文名称

BS EN1122:2001:湿法消解测定塑料中的镉BS EN 1122:2001:Plastics-determination of cadmium-Wet decomposition method方法3005A:FLAA,ICP方法分析酸式消解水中的总溶解金属METHOD 3005A:ACID DIGESTION OF WATERS FOR TOTAL RECVERABLE OR DISSOLVED METALS FOR ANALYSIS BY FLAA OR ICP SPECTROSCOPY方法3010A: FLAA,ICP方法分析酸式消解水样和蒸馏样中的总金属METHOD 3010A:ACID DIGESTION OF AQUEOUS SAMPLES AND EXTRACTS FOR TOTAL METALS FOR ANALYSIS BY FLAA OR ICP SPECTROSCOPY方法3015:微波酸式消解水样和蒸馏液METHOD 3015:MICROWAVE ASSISTED ACID DIGESTION OF AQUEOUS SAMPLES AND EXTRACTS 方法3020A:G FAA方法分析酸式消解水样和蒸馏样中的总金属METHOD 3010A:ACID DIGESTION OF AQUEOUS SAMPLES AND EXTRACTS FOR TOTAL METALS FOR ANALYSIS BY GFAA SPECTROSCOPY方法3031:AAS,ICP分析酸式消解石油中的金属元素METHOD 3031:ACID DIGESTION OF OILS FOR METALS ANALYSIS BY ATOMIC ABSORPTION OR ICP SPECTROMETRY方法3040A:石油,油脂,石蜡的消解程序METHOD 3040A:DISSOLUTION PROCEDURE FOR OILS, GREASES, OR WAXES方法3050B:沉淀物,淤泥,土壤的酸式消解METHOD 3050B:ACID DIGESTION OF SEDIMENTS, SLUDGES, AND SOILS方法3051:沉淀物,淤泥,土壤石油的微波酸式消解METHOD 3051:MICROWAVE ASSISTED ACID DIGESTION OF SEDIMENTS SLUDGES, SOILS, AND OILS方法3052:硅酸盐和有机质的微波酸式消解METHOD 3052:MICROWAVE ASSISTED ACID DIGESTION OF SILICEOUS AND ORGANICALLY BASED MATRICES方法3060:六价铬的碱式消解METHOD 3060A:ALKALINE DIGESTION FOR HEXAVALENT CHROMIUM方法3500B:有机萃取和样品制备METHOD 3500B:ORGANIC EXTRACTION AND SAMPLE PREPARATION方法3510C:分液漏斗的液—液萃取METHOD 3510C :SEPARATORY FUNNEL LIQUID-LIQUID EXTRACTION方法3520C:连续液-液萃取METHOD3520C:CONTINUOUS LIQUID-LIQUID EXTRACTION方法3535:固相萃取METHOD 3535:SOLID-PHASE EXTRACTION (SPE)方法3540C:索氏萃取SOXHLET EXTRACTION方法3541:AUTOMATED SOXHLET EXTRACTION方法3542:用方法0010收集半挥发性分析物的萃取物METHOD 3542:EXTRACTION OF SEMIVOLATILE ANALYTES COLLECTED USING METHOD 0010(MLDIFIED METHOD 5 SAMPLING TRAIN)方法3545:密闭流动萃取METHOD 3545:PRESSURIZED FLUID EXTRACTION (PFE)方法3546:微波萃取METHOD 3546:MICROWAVE EXTRACTION方法3550B:超声波萃取METHOD 3550B:ULTRASONIC EXTRACTION方法3560:超临界流动萃取石油中的中回收物METHOD 3560:SUPERCRITICAL FLUID EXTRACTION OF TOTAL RECOVERABLE PETROLEUM HYDROCARBONS方法3561:多环芳烃的超临界流动萃取METHOD 3561:SUPERCRITICAL FLUID EXTRACTION OF POLYNUCLEAR AROMATIC HYDROCARBONS方法3580:废物稀释METHOD 3580A:WASTE DILUTION方法3585:挥发性有机物的废物稀释METHOD 3585:WASTE DILUTION FOR VOLATILE ORGANICS方法3600C:清除METHOD 3600C:CLEANUP方法3610B:矾土的清除METHOD 3610B:ALUMINA CLEANUP方法3611B:柱状矾土的清除和石油废弃物的分离METHOD 3611B:ALUMINA COLUMN CLEANUP AND SEPARATION OF PETROLEUM WASTES方法3520B:硅酸镁的清除METHOD 3520B:FLORISIL CLEANUP方法3630C:硅胶的清除METHOD 3630C:SILICA GEL CLEANUP方法3640A:渗入硅胶的清除METHOD 3640A:GEL-PERMEATION CLEANUP方法3650B:酸碱的分离清除METHOD 3650B:ACID-BASE PARTITION CLEANUP方法3660B:硫磺的清除METHOD3660B:SULFUR CLEANUP方法3665A:硫酸,高锰酸的清除METHOD 3665A:SULFURIC ACID/PERMANGANATE CLEANUP方法3810:顶部空间METHOD 3810:HEADSPACE方法3820:16烷萃取和净化有机物的屏蔽METHOD 3820:HEXADECANE EXTRACTION AND SCREENING OF PURGEABLE ORGANICS方法7000A:原子吸收方法METHOD 7000A:ATOMIC ABSORPTION METHODS方法7130:镉(原子吸收,直接吸收)METHOD7130:CADMIUM (ATOMIC ABSORPTION, DIRECT ASPIRATION)方法7130A:镉(原子吸收,炉子技术)METHOD7131A:CADMIUM (ATOMIC ABSORPTION, FURNACE TECHNIQUE)方法7190:铬(原子吸收,直接吸收)METHOD7190:CHROMIUM (ATOMIC ABSORPTION, DIRECT ASPIRATION)方法7191:铬(原子吸收,炉子技术)METHOD7191:CHROMIUM (ATOMIC ABSORPTION, FURNACE TECHNIQUE)方法7196A:六价铬(比色)METHOD 7196A:CHROMIUM, HEXAVALENT (COLORIMETRIC)方法7420:铅(原子吸收,直接吸收)方法7420:LEAD (ATOMIC ABSORPTION, DIRECT ASPIRATION)方法7421:铅(原子吸收,炉子技术)METHOD 7421:LEAD (ATOMIC ABSORPTION, DIRECT ASPIRATION)方法7470A:废水中的汞(冷原子蒸汽技术)METHOD 7470A:MERCURY IN LIQUID WASTE (MANUAL COLD-VAPOR TECHNIQUE)方法7471A:固体和固体废弃物中的汞(冷原子蒸汽技术)METHOD 7471A:MERCURY IN SOLID OR SEMISOLID WASTE (MANUAL COLD-VAPOR TECHNIQUE) 方法7473 :热分解原子吸收光谱法测定固体和液体样品中的汞METHOD 7473:MERCURY IN SOLIDS AND SOLUTIONS BY THERMAL DECOMPODITION AMALGAMATION, AND ATOMIC ABSORPTION SPECTROPHOTOMETRY方法8000B:限定色谱分离METHOD 8000B:DETERMINATIVE CHROMATOGRAPHIC SEPARATIONS方法8081A:气相色谱分析有机氯沙虫剂METHOD 8081A:ORGANOCHLORINE PESTICIDES BY GAS CHROMATOGRAPHY方法8081B:气相色谱分析有机氯沙虫剂METHOD 8081B:ORGANOCHLORINE PESTICIDES BY GAS CHROMATOGRAPHY方法8082:气相色谱分析多氯联苯METHOD 8082:POLYCHLORINATED BIPHENYLS (PCBs) BY GAS CHROMATOGRAPHY方法8082A:气相色谱分析多氯联苯METHOD 8082A:POLYCHLORINA BIPHENYLS (PCBs) BY GAS CHROMATOGRAPHY方法8260B:气相色谱/质谱分析挥发性有机化合物METHOD 8260B:VOLATILE ORGANIC COMPOUNDS BY GAS CHROMATOGRAPHY/MASS SPECTROMETRY (GC/MS)。

商务部公告2003年第21号--对原产于日本、韩国和美国的进口甲苯二

商务部公告2003年第21号--对原产于日本、韩国和美国的进口甲苯二

商务部公告2003年第21号--对原产于日本、韩国和美国的进口甲苯二异氰酸酯(TDI)反倾销调查的初裁决定【法规类别】倾销与反倾销【发文字号】商务部公告2003年第21号【发布部门】商务部【发布日期】2003.06.10【实施日期】2003.06.10【时效性】现行有效【效力级别】XE0303中华人民共和国商务部公告(2003年第21号)根据2001年11月通过的《中华人民共和国反倾销条例》(以下简称《中华人民共和国反倾销条例》)的规定,经商原国家经济贸易委员会,原对外贸易经济合作部于2002年5月22日发布公告,决定对原产于日本、韩国和美国的进口甲苯二异氰酸酯(TDI)(型号为TDI80/20)(以下称“被调查产品”)进行反倾销调查。

该被调查产品在中华人民共和国海关进口税则号中列为:29291010。

原对外贸易经济合作部对被调查产品是否存在倾销及倾销幅度进行了调查,原国家经济贸易委员会对被调查产品是否对国内产业造成损害及损害程度进行了调查。

在案件调查期限内,经十届人大一次会议批准,由新组建的商务部承担反倾销调查职能。

商务部根据调查结果和《中华人民共和国反倾销条例》第24条的规定作出初裁决定(见附件)。

现将有关事项公告如下:一、初裁决定商务部初裁决定被调查产品存在倾销,并对国内产业造成实质损害,同时认定倾销和实质损害之间存在因果关系。

二、对各公司初裁确定的倾销幅度(一)日本1、聚氨酯工业株式会社(NIPPON POLYURETHANE INDUSTRY CO.,LTD) 28%2、三井武田化学株式会社(MITSUI TAKEDA CHEMICAL,INC.) 19%3、其他日本公司:49%(二)韩国1、东洋制铁化学株式会社 (DC Chemical Co.,Ltd) 22%2、韩国FINE CHEMICAL株式会社(Korea Fine Chemical Co,Ltd.) 6%3、其他韩国公司:22%(三)美国1、美国巴斯夫公司 (BASF Corporation) 28%2、美国拜耳公司(Bayer Corporation) 23%3、其他美国公司: 28%三、临时反倾销措施根据《中华人民共和国反倾销条例》第28条和29条的规定,商务部决定采用现金保证金形式实施临时反倾销措施。

绪论

绪论

• 过氧化反应,过量自由基等导致错配 • DNA-RNA-protein – Cancer • 基因片段
结肠癌
• 明尼苏达州罗切斯特梅欧医院的研究人员 Wanguo Liu博士发现一种新基因AXIN2, 该基因的突变可导致结肠直肠癌的发生。


Michael C. Newman
• • • • Professor of Marine Science B.A., University of Connecticut Ph.D. Rutgers University Memberships Society of Environmental Toxicology and Chemistry (SETC) Email: newman@ Office: Chesapeake Bay Hall, S110 Phone: (804) 684-7725
Cancer worldwide
• Cancer is a leading cause of death worldwide. From a total of 58 million deaths worldwide in 2005, cancer accounts for 7.6 million (or 13%) of all deaths. The main types of cancer leading to overall cancer mortality are: • lung (1.3 million); • Stomach (almost 1 million); • Liver (662,000); • Colon 结肠 (655,000) and • Breast (502,000). • Deaths from cancer in the world are projected to continue rising, with an estimated 9 million people dying from cancer in 2015 and 11.4 million dying in 2030. • http://www.who.int/mediacentre/factsheets/fs297/en/

氧化镍_戊基黄药体系的浮选和表面分析

氧化镍_戊基黄药体系的浮选和表面分析

氧化镍(Ò)/戊基黄药体系的浮选和表面分析M#L#拉克利基等摘要微浮选试验结果表明,在pH4~8范围内戊基黄药可以浮选氧化镍(Ò)。

Zeta电位测量数据证实了,黄药的存在使得其等电点向酸性范围偏移。

固态吸收红外光谱(KBr压片法)证明了,AmX中末端硫阴离子以单配位方式与Ni2+离子键合。

应用固态红外吸收光谱时,AmX的浓度需要大大高于浮选中使用的浓度。

顶空气相红外光谱可在浮选所用的捕收剂浓度下进行分析。

关键词浮选化学吸附捕收剂黄药Zeta电位概述21世纪,贱金属非硫化矿资源的重要性增大了,其中包括天然产出的资源(如铜、锌和镍的氧化矿石)和二次资源(如冶金渣)。

非硫化矿物通常是亲水的,所以浮选它们比浮选硫化矿物要难得多。

例如,用短链巯基捕收剂(乙基黄药)可成功浮选硫化矿物,而需要用长链捕收剂(脂肪酸或胺)浮选非硫化矿物。

对表面氧化的硫化矿物,需要预先用硫离子活化(硫化),然后与巯基捕收剂搅拌再进行浮选。

已经叙述过用金属阳离子来活化氧化物。

用铅离子预先活化后用黄药浮选石英就是一个实例。

众所周知,黄药可与自然金属反应,戊基黄药可浮选由离析法处理氧化镍矿石生成的金属镍。

本文将报导有关氧化镍/戊基黄药浮选实例。

过去的研究只涉及到辛基黄药在NiO上的吸附和非巯基捕收剂浮选NiO。

本文提出了微浮选试验结果。

同时,联合应用电泳(Zeta电位)和红外光谱测量验证了戊基黄药在氧化镍表面上的存在,并确定了其表面上生成物质的成份。

1试验111物料试验中所用氧化镍(Ò)纯度为99%或991999%,粒度为-44L m。

带6个结晶水的硫酸镍(Ò)纯度为98%。

红外光谱测定所用的溴化钾纯度高于99%。

带有结晶水的碳酸钠纯度为100%,氢氧化钠纯度为97%。

硝酸和盐酸为化学分析纯级。

起泡剂Dow froth250C由Dow化学品公司供给。

戊基钾黄药应用前经再结晶提纯。

112微浮选浮选在由氢氧化钠或盐酸调节的pH4、6、8、10和12条件下进行。

玩具安全标准

玩具安全标准

玩具安全标准1.儿童玩具的年龄范围:0 14岁.2.儿童玩具安全标准。

2.1美国—消费品安全公署(CPSC)制定之”玩具及儿童用品条例”.ASTMF963-86玩具安全标准.各种金属元素的规定限量列于下表:part per million-—ppm元素名称铅LEAD(PB) p lumbum可接受之含量0。

060 或600PPM 2.2加拿大--危险品(玩具) 条例由加拿大标准学会(GSA) 制定.2。

3澳洲—-AS.1647玩具安全标准.2.4欧洲—-欧洲共市协调标准EN71(88年版)。

-—英国BS5665 —-法国NF51—2022.5中国(PRC)--GB6675—-86玩具安全.3.玩具之毒性(TOXIGOLOGY)3。

1有毒物质-—制造玩具的物料及合成玩具的各部分都必须清洁,以防任何细菌的传染.3.2重金属成份—-所有制造玩具用的物料,包括塑料,色粉,原料,电度层及润滑济等,均不能含有超量的重金属成份,一般以百分比重(PPM)作计量单位.砒ARSENIC(AS)0。

060 或600PPM镉CADMIUM(CD) 0.060 或600PPM汞MERCURY(HG) 0。

060 或600PPM硒selenium(SE)0。

060 或600PPMAS+CD+HG+SE的总量0.060 或600PPM可溶解的重金属化合物锑SB 0。

025 或250PPM砒AS 0.010 或100PPM钡BA 0。

050 或500PPM硌CR 0.025 或250PPM镉CD 0.010 或100PPM汞HG 0.010 或100PPM4.易燃性能(FLAMMABILITY)——此标准的目的是减低儿童因玩弄易燃玩具而导致灼伤的机会。

4.1 ASTMF 963-86A.玩具成品(包括布类及非布类玩具):—-将玩具平放燃烧,若速度超过每秒0.1英寸(2。

5MM)便不合格。

B.布料:将一块2X6布料平放在已用车缝线绕好的”U"形燃烧架上,在开口的一端点火规格要求:燃烧速度不可大于于10IN/MIN4.2 EN71-—主要针对玩具面具,假发,假胡须,玩具服装,玩具营帐及布面填充玩具。

关于SGS和ROHS

关于SGS和ROHS

RoHS指令检测RoHS是《电气、电子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)的英文缩写。

目前主要针对电子电气产品中的铅Pb、镉Cd、汞Hg、六价铬Cr6+、多溴联苯PBBs、多溴联苯醚PBDEs六种有害物质进行限制。

以后也将对更多的有害物质进行限制。

该指令由欧洲议会及理事会提出,欧盟成员国将于2006年7月1日起强制实施。

届时将禁止含有有害重金属及以多溴联苯、多溴联苯醚作阻燃剂的电子电气产品进入欧盟市场。

WEEE是《电子电气产品的废弃指令》(Waste Electrical and Electronic Equipment)的英文缩写。

该指令也由欧洲议会及理事会提出,欧盟成员国于2005年8月13日起已经开始强制实施。

其主要目的是预防废弃物的产生,其次是为方便废弃物进行再回收、再使用、再制造,减少资源浪费。

RoHS指令的函盖范围为AC1000V、DC1500V以下的由目录所列出的电子、电气产品:1、大型家用电器:冰箱、洗衣机、微波炉、空调等2、小型家用电器:吸尘器、电熨斗、电吹风、烤箱、钟表等3、IT及通讯仪器:计算机、传真机、电话机、手机等4、民用装置:收音机、电视机、录象机、乐器等5、照明器具:除家庭用照明外的荧光灯等,照明控制装置6、电动工具:电钻、车床、焊接、喷雾器等(需安装的大型产业工具除外)7、玩具/娱乐、体育器械:电动车、电视游戏机、自动赌博机等8、医疗器械:放射线治疗仪、心电图测试仪、分析仪器等9、监视/控制装置:烟雾探测器、恒温箱、工厂用监视控制机等10、自动售货机其中,RoHS指令暂不适用第8、9两条。

欧洲目前已经制定了一些化学物质法规,主要有:76/769/EEC(关于危险物质及调剂的上市和使用限制的指令);91/157/EEC(关于含有特定危险物质的电池/蓄电池的指令);94/62/EC(关于包装及废弃物的指令);2000/53/EC(报废汽车ELV指令);2002/96/EC(报废电子电气指令WEEE指令);2002/95/EC(限制电子电气产品使用特定有害物质的指令ROHS指令)。

中华人民共和国2003年发布的化学试剂国家标准

中华人民共和国2003年发布的化学试剂国家标准

中华人民共和国2003年发布的化学试剂国家标准
佚名
【期刊名称】《化学试剂》
【年(卷),期】2004(26)4
【总页数】1页(P244-244)
【关键词】中华人民共和国;化学试剂;2003
【正文语种】中文
【中图分类】O6
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4.关于发布行业标准《建筑工程饰面砖粘结强度检验标准》的公告中华人民共和国建设部公告第826号/关于发布国家标准《水泥基灌浆材料应用技术规范》的公告中华人民共和国住房和城乡建设部公告第7号/关于发布国家标准《盾构法隧道施
工与验收规范》的公告中华人民共和国住房和城乡建设部 [J],
5.近年来发布实施的化学试剂国家标准行业标准 [J], 无
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COMMISSION DIRECTIVE2003/2/ECof6January2003relating to restrictions on the marketing and use of arsenic(tenth adaptation to technical progressto Council Directive76/769/EEC)Text withEEA relevance)THE COMMISSION OF THE EUROPEAN COMMUNITIES,Having regard to the Treaty establishing the European Community,Having regard to Council Directive76/769/EEC of27July 1976on the approximation of the laws,regulations and administrative provisions of the Member States relating to restrictions on the marketing and use of certain dangerous substances and preparations(1),as last amended by Commis-sion Directive2002/62/EC(2)and in particular Article2(a) thereof,introduced by Council Directive89/678/EEC(3),Whereas:(1)Council Directive89/677/EEC(4)amending for theeighth time Directive76/769/EEC places certain restric-tions on the marketing and use of arsenic.(2)A risk assessment and an analysis of advantages anddrawbacks of further restrictions on arsenic in certainwood preservatives(5)were carried out in the frameworkof a review of Community legislation concerning the useof arsenic compounds for wood preservation followingthe accession of Austria,Finland and Sweden to theEuropean Union in1995.(3)The risk assessment was referred to the ScientificCommittee on Toxicity,Ecotoxicity and the Environment(CSTEE)for peer review(6)and the CSTEE concludedthat the main risks had been identified correctly.Theserisks included those to human health from the disposalof wood treated with wood preservatives containingcopper,chrome and arsenic(CCA)and in particular risksto children's health from the use of CCA-treated woodin playground equipment.A risk to the aquatic environ-ment in certain marine waters was also identified.(4)The CSTEE further advised that in the light of a seriousknowledge gapin relation to arsenic-treated wood inlandfills it would be advisable to exercise caution bylimiting the use of arsenic-based wood preservation tothose situations where it is absolutely necessary.(5)In a further consideration of the health effects ofarsenic(7)the CSTEE has concluded that the substance isboth genotoxic and a well known carcinogen,and that itmay be appropriate to consider that no threshold existsfor carcinogenic effect.(6)Waste CCA-treated wood has been classified as hazar-dous waste pursuant to Commission Decision2000/532/EC of3May2000replacing Decision94/3/ECestablishing a list of wastes pursuant to Article1(a)ofCouncil Directive75/442/EEC on waste and CouncilDecision94/904/EC establishing a list of hazardouswaste pursuant to Article1(4)of Council Directive91/689/EC on hazardous waste(8)as last amended byCouncil Decision2001/573/EC(9).(7)Directive98/8/EC of the European Parliament and of theCouncil of16February1998concerning the placing ofbiocidal products on the market(10)lays down provi-sions for harmonising the authorisation of biocides atCommunity level and Commission Regulation(EC)No1896/2000of7September2000on the first phase ofthe programme referred to in Article16(2)of Directive98/8/EC of the European Parliament and of the Councilon biocidal products(11)requires wood preservatives tobe evaluated as a priority in the review programmeestablished under Directive98/8/EC.Arsenic has beenidentified and notified as an active substance within thetime limit set out in Regulation(EC)No1896/2000.Acomplete dossier for evaluation of arsenic as an existingsubstance will have to be presented by28March2004.(8)With regard to the risk assessment and taking accountof the precautionary principle,pending harmonisation ofrules under Directive98/8/EC or a Decision pursuant toArticle6(3)of Regulation(EC)No1896/2000,it isnecessary to adapt the restrictions on arsenic in Directive76/769/EEC to technical progress.This Directive doesnot apply to CCA-treated wood already in place.(1)OJ L262,27.9.1976,p.201.(2)OJ L183,12.7.2002,p.58.(3)OJ L398,30.12.1989,p.24.(4)OJ L398,30.12.1989,p.19.(5)Assessment of the Risks to Health and to the Environment ofArsenic in Wood Preservatives and of the Effects of Further Restric-tions on its marketing and use,1998.(6)http://europa.eu.int/comm/food/fs/sc/sct/out18_en.html.(7)http://europa.eu.int/comm/food/fs/sc/sct/out106_en.html.(8)OJ L226,6.9.2000,p.3.(9)OJ L203,28.7.2001,p.18.(10)OJ L123,24.4.1998,p.1.(11)OJ L228,8.9.2000,p.6.(9)This Directive should apply without prejudice toCommunity legislation laying down minimum require-ments for the protection of workers,in particular,Council Directive89/391/EEC of12June1989on theintroduction of measures to encourage improvements inthe safety and health of workers at work(1),CouncilDirective90/394/EEC of28June1990on the protec-tion of workers from the risks related to exposure tocarcinogens at work(Sixth individual Directive withinthe meaning of Article16(1)of Directive89/391/EEC)(2),as last amended by Directive1999/38/EC(3)and Council Directive98/24/EC of7April1998on theprotection of workers from chemical agents at work(14th individual Directive within the meaning of Article16(1)of Directive89/391/EEC)(4).(10)The measures provided for in this Directive are in accor-dance with the opinion of the Committee for the adapta-tion to technical progress of directives on the removal oftechnical barriers to trade in dangerous substances andpreparations,HAS ADOPTED THIS DIRECTIVE:Article1Annex I to Directive76/769/EEC is hereby amended as set out in the Annex to this Directive.Article2Member States shall adopt and publish the provisions necessary to comply with this Directive by30June2003at the latest. They shall forthwith inform the Commission thereof.They shall apply these provisions by30June2004at the latest.When Member States adopt those provisions,they shall contain a reference to this Directive or be accompanied by such a refer-ence on the occasion of their official publication.Member States shall determine how such reference is to be made.Article3This Directive shall enter into force on the20th day following that of its publication in the Official Journal of the European Communities.Article4This Directive is addressed to the Member States.Done at Brussels,6January2003.For the CommissionErkki LIIKANENMember of the Commission1p.1.(2)OJ L196,26.7.1990,p.1.(3)OJ L138,1.6.1999,p.66.(4)OJ L131,5.5.1998,p.11.ANNEXAnnex I to Directive1976/769/EEC,point20is replaced by the following:‘20.Arsenic compounds 1.May not be used as substances and constituents of preparations intended for use:(a)To prevent the fouling by micro-organisms,plants or animals of:—the hulls of boats,—cages,floats,nets and any other appliances or equipment used for fish orshellfish farming,—any totally or partly submerged appliances or equipment;(b)in the preservation of wood.Furthermore,wood so treated may not be placed onthe market;(c)however,by way of derogation:(i)Relating to the substances and preparations in the preservation of wood:these may only be used in industrial installations using vacuum or pressure toimpregnate wood if they are solutions of inorganic compounds of the copper,chromium,arsenic(CCA)type C.Wood so treated may not be placed on themarket before fixation of the preservative is completed.(ii)Relating to wood treated with CCA solutions in industrial installationsaccording to point(i):this may be placed on the market for professional andindustrial use provided that the structural integrity of the wood is required forhuman or livestock safety and skin contact by the general public during itsservice life is unlikely:—as structural timber in public and agricultural buildings,office buildings,and industrial premises,—in bridges and bridgework,—as constructional timber in freshwater areas and brackish waters e.g.jetties and bridges,—as noise barriers,—in avalanche control,—in highway safety fencing and barriers,—as debarked round conifer livestock fence posts,—in earth retaining structures,—as electric power transmission and telecommunications poles,—as underground railway sleepers.Without prejudice to the application of other Community provisions on theclassification,packaging and labelling of dangerous substances and prepara-tions,all treated wood placed on the market shall be individually labelled“Forprofessional and industrial installation and use only,contains arsenic”.Inaddition,all wood placed on the market in packs shall also bear a labelstating“Wear gloves when handling this wood.Wear a dust mask and eyeprotection when cutting or otherwise crafting this wood.Waste from thiswood shall be treated as hazardous by an authorised undertaking”.(iii)Treated wood referred to under points(i)and(ii)may not be used:—in residential or domestic constructions,whatever the purpose,—in any application where there is a risk of repeated skin contact,—in marine waters,—for agricultural purposes other than for livestock fence posts and struc-tural uses in accordance with point(ii),—in any application where the treated wood may come into contact withintermediate or finished products intended for human and/or animalconsumption.2.May not be used as substances and constituents of preparations intended for use inthe treatment of industrial waters,irrespective of their use.’。

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