C72 生产环境安全卫生设施 标准查询与下载

AQ 4220-2012 石材加工工艺防尘技术规范

本标准规定了石材加工工艺的防尘技术措施和管理要求。 本标准适用于石材加工中具有粉尘职业危害的工艺和作业过程。

Technical code of dust control for stone processing

AQ 4221-2012 粮食加工防尘防毒技术规范

本标准规定了粮食加工企业防尘防毒的基本要求、技术措施和管理。 本标准适用于粮食加工过程（不包括油脂加工）中的防尘防毒技术要求及管理措施。

Technical code of dust and poison control for grain processing

AQ 4222-2012 酒类生产企业防尘防毒技术规范

本标准规定了酒类生产企业防尘防毒的基本要求、技术措施和管理。 本标准适用于饮料酒（发酵酒、蒸馏酒、配制酒）生产过程中的防尘防毒技术要求及管理措施。

Technical requirement of dust and poison control for wine production enterprises

DIN EN 1540:2012 车间曝光.术语.三种语言版本 EN 1540-2011

Workplace exposure - Terminology; Trilingual version EN 1540:2011

DIN 33897-4:2009 工作场所空气.散装材料含尘量测定用常规方法.第4部分:错流中的反复下落

Workplaces atmospheres - Routine methods for the determination of dustiness of bulk materials - Part 4: Repeated drop in the cross-flow

KS I ISO 11041:2008 车间空气.砷、砷化合物悬浮粒子和三氧化二砷蒸气的测定.氢化法和原子吸收光谱法

이 표준은 연속 흐름식 수소화물 발생 또는 흐름 분사 분석식 수소화물 발생과 원자 흡광 분

Workplace air－Determination of particulate arsenic and arsenic compounds and arsenic trioxide vapour－Method by hydride generation and atomic absorption spectrometry

KS I ISO 11174:2008 车间空气和镉化合物悬浮粒子的测定.燃烧和电热原子吸收光谱法

이 표준은 불꽃이나 전열 원자 흡광 분광법을 사용해 작업장 공기 중의 입자상 카드뮴과 카드

Workplace air－Determination of particulate cadmium and cadmium compounds－Flame and electrothermal atomic absorption spectromet method

BS EN ISO 13857:2008 机械安全性.防止上,下臂触及危险区的安全距离

Safety of machinery - Safety distances to prevent hazard zones being reached by upper and lower limbs

KS I ISO 17734-2:2007 在空气中用液相色谱法和质谱学对有机氮化合物的测定.第2部分:用二丁胺和乙基氯甲酸酯衍生物的胺和氨基异氰酸酯

이 규격은 작업장의 공기 중에서 공기로 운반되는 아민 및 아미노이소시아네이트의 시료 채취

Determination of organonitrogen compounds in air using liquid chromatography and mass spectrometry-Part 2:Amines and aminoisocyanates using dibutylamine and ethyl chloroformate derivatives

ASTM F50-07 用可探测单个亚微米及较大粒子的仪器在灰尘控制区域和无菌室中连续测定空气中粒子的大小及计数用标准实施规程

1.1 This practice covers the determination of the particle concentration, by number, and the size distribution of airborne particles in dust-controlled areas and clean rooms, for particles in the size range of approximately 0.01 to 5.0 m. Particle concentrations not exceeding 3.5 106 particles/m3 (100 000/ft 3) are covered for all particles equal to and larger than the minimum size measured.1.2 This practice uses an airborne single particle counting device (SPC) whose operation is based on measuring the signal produced by an individual particle passing through the sensing zone. The signal must be directly or indirectly related to particle size. Note 1The SPC type is not specified here. The SPC can be a conventional optical particle counter (OPC), an aerodynamic particle sizer, a condensation nucleus counter (CNC) operating in conjunction with a diffusion battery or differential mobility analyzer, or any other device capable of counting and sizing single particles in the size range of concern and of sampling in a cleanroom environment.1.3 Individuals performing tests in accordance with this practice shall be trained in use of the SPC and shall understand its operation.1.4 Since the concentration and the particle size distribution of airborne particles are subject to continuous variations, the choice of sampling probe configuration, locations and sampling times will affect sampling results. Further, the differences in the physical measurement, electronic and sample handling systems between the various SPCs and the differences in physical properties of the various particles being measured can contribute to variations in the test results. These differences should be recognized and minimized by using a standard method of primary calibration and by minimizing variability of sample acquisition procedures.1.5 Sample acquisition procedures and equipment may be selected for specific applications based on varying cleanroom class levels. Firm requirements for these selections are beyond the scope of this practice; however, sampling practices shall be stated that take into account potential spatial and statistical variations of suspended particles in clean rooms. General references to cleanroom classifications follow Federal Standard 209E, latest revision. Where airborne particles are to be characterized in dust-controlled areas that do not meet these classifications, the latest revision of the pertinent specification for these areas shall be used.This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use. For specific hazards statements, see Section 8.

Standard Practice for Continuous Sizing and Counting of Airborne Particles in Dust-Controlled Areas and Clean Rooms Using Instruments Capable of Detecting Single Sub-Micrometre and Larger Particles

BS EN 12841:2006 个人防跌落设备.绳索通道系统.绳索调整设备

This European Standard applies to rope adjustment devices intended for use in rope access systems. It specifies the requirements, test methods, marking and information supplied by the manufacturer. Rope adjustment devices conforming to this European Standard may be designed for the use of one person, or in case of rescue, for two persons simultaneously. The rope adjustment devices as specified are not suitable for use in a fall arrest system.

Personal fall protection equipment - Rope access systems - Rope adjustment devices

ISO 17734-2:2006 在空气中用液相色谱法和质谱学对有机氮化合物的测定.第2部分:用二丁胺和乙基氯甲酸酯衍生物的胺和氨基异氰酸酯

This part of ISO 17734 gives general guidance for the sampling and analysis of airborne amines and aminoisocyanates in workplace air. It is strongly recommended that the determination of amines and aminoisocyanates is made together with the determination of isocyanates in air, using DBA as a reagent (ISO 17734-1). The method can be used for simultaneous determinations of amines, 4,4'-methylenediphenyldiamine (4,4'-MDA), 2,4- and 2,6-toluenediamine (2,4-, 2,6-TDA) and 1,6-hexamethylenediamine (1,6-HDA), and compounds containing both isocyanate and amine groups, 4,4'-methylenediphenyl aminoisocyanate (4,4'-MAI), 2,4-, 4,2- and 2,6-toluene aminoisocyanate (2,4, 4,2, 2,6-TAI), 1,6-hexamethylene aminoisocyanate (1,6-HAI). The method is suitable for collecting amines and aminoisocyanates in both the gas and particle phases. The instrumental detection limit for the amines is about 50 fmol and for the aminoisocyanate, it is about 3 fmol. For a 15-1 air sample, this corresponds to 0,4 ng-rrr3 for TDA and 0,03 ngm-3forTAI.

Determination of organonitrogen compounds in air using liquid chromatography and mass spectrometry Part 2: Amines and aminoisocyanates using dibutylamine and ethyl chloroformate derivatives (Second Edition)

KS I ISO 15202-3:2005 车间空气.感应耦合等离子体原子发射光谱法对气载颗粒物中金属及类金属的测定.第3部分:分析

이 규격은 KS M ISO 15202-1에 제시된 방법에 따라 포집된 공기 중 입자상 물질

Workplace air ― Determination of metals and metalloids in airborne particulate matter by inductively coupled plasma atomic emission spectrometry ― Part 3: Analysis

KS I ISO 17733:2005 车间空气.汞和无机汞化合物的测定.低温蒸气原子吸收分光光度测定法或原子荧光分光光度测定法

이 규격은 작업장에서 수은 증기와 무기 수은 화합물의 시간 가중 평균 질량 농도의 결정을

Workplace air－Determination of mercury and inorganic mercury compounds－Method by cold－vapour atomic absorption spectrometry or atomic fluorescence spectrometry

ISO 17733:2004 车间空气.汞和无机汞化合物的测定.低温蒸气原子吸收分光光度测定法或原子荧光分光光度测定法

This International Standard specifies a procedure for determination of the time-weighted average mass concentration of mercury vapour and inorganic mercury compounds in workplace air. Mercury vapour is collected on a solid sorbent using either a diffusive badge or a pumped sorbent tube. Particulate inorganic mercury compounds, if present, are collected on a quartz fibre filter. Samples are analysed using either cold vapour atomic absorption spectrometry (CVAAS) or cold vapour atomic fluorescence spectrometry (CVAFS) after acid dissolution of the mercury collected. This International Standard is applicable to the assessment of personal exposure to mercury vapour and/or particulate inorganic mercury compounds in air for comparison with long-term or short-term exposure limits for mercury and inorganic mercury compounds and for static (area) sampling. The lower limit of the working range of the procedure is the quantification limit. This is determined by the sampling and analysis methods selected by the user, but it is typically in the range 0,01 µg to 0,04 µg of mercury (see 13.1). The upper limit of the working range of the procedure is determined by the capacity of the diffusive badge, sorbent tube or filter used for sample collection, but it is at least 30 µg of mercury (see 13.2). The concentration range of mercury in air for which this International Standard is applicable is determined in part by the sampling method selected by the user, but it is also dependent on the air sample volume. The diffusive badge method is not applicable to measurements of mercury vapour when chlorine is present in the atmosphere, e.g. in chloralkali works, but chlorine does not interfere with the pumped sorbent tube method (see 13.11.1). Gaseous organo-mercury compounds could cause a positive interference in the measurement of mercury vapour (see 13.11.2). Similarly, particulate organo-mercury compounds and gaseous organo-mercury compounds adsorbed onto airborne particles could cause a positive interference in the measurement of particulate inorganic mercury compounds (see 13.11.3).

Workplace air - Determination of mercury and inorganic mercury compounds - Method by cold-vapour atomic absorption spectrometry or atomic fluorescence spectrometry

ISO 15202-3:2004 车间空气.感应耦合等离子体原子发射光谱法对气载颗粒物中金属及类金属的测定.第3部分:分析

This part of ISO 15202 specifies a procedure for the use of inductively coupled plasma atomic emission spectrometry for analysing test solutions prepared as prescribed in ISO 15202-2 from samples of airborne particulate matter collected as specified in ISO 15202-1. Method development, performance checks and a routine analysis method are specified. This part of ISO 15202 is applicable for the assessment of workplace exposure to metals and metalloids for comparison with limit values (see e.g. EN 689[1], ASTM E 1370[2], etc.). The following is a non-exclusive list of metals and metalloids for which limit values have been set (see Reference [3]), and for which one or more of the sample dissolution methods specified in ISO 15202-2 and the analytical procedure described in this part of ISO 15202 are applicable. However, there is no information available on the effectiveness of any of the sample dissolution methods specified in ISO 15202-2 for those elements in italics. aluminium calcium magnesium selenium tungsten antimony chromium manganese silver uranium arsenic cobalt mercury sodium vanadium barium copper molybdenum strontium yttrium beryllium hafnium nickel tantalum zinc bismuth indium phosphorus tellurium zirconium boron iron platinum thallium caesium lead potassium tin cadmium lithium rhodium titanium NOTE ISO 15202 is not applicable to determination of elemental mercury, since mercury vapour is not collected using the sampling method specified in ISO 15202-1. The procedure is suitable for assessment of exposure against the long-term exposure limits for most of the metals and metalloids listed above when sampling at a typical flow rate of 2 lmin for sampling times in the range 30 min to 8 h and for assessment of exposure against the short-term exposure limits, where applicable (see 10.4). The procedure suffers from no significant spectral interferences (see 10.5), provided that suitable analytical wavelengths are used. However, inaccurate background correction and/or inadequate matrix-matching can adversely affect results.

Workplace air - Determination of metals and metalloids in airborne particulate matter by inductively coupled plasma atomic emission spectrometry - Part 3: Analysis

ASTM D5836-03 测定工作场所大气中2,4-二异氰酸甲苯(2,4-TDI)和2,6-二异氰酸甲苯(2,6-TDI)的标准试验方法

Diisocyanates are used in the production of polyurethane foams, plastics, elastomers, surface coatings, and adhesives (5,6). It has been estimated that the production of TDI will steadily increase during the future years. Diisocyanates are irritants to eyes, skin, and mucous membrane and are respiratory sensitizers. Chronic exposure to low concentrations of diisocyanates produces an allergic sensitization which may progress into asthmatic bronchitis (7,8). The Occupational Safety and Health Administration (OSHA) has a permissible exposure limit for 2,4-TDI of 0.02 ppm or 0.14 mg/m3 as a ceiling limit (9). The American Conference of Governmental Industrial Hygienists (ACGIH) has a Threshold Limit Value (TLV) of 0.005 ppm or 0.036 mg/m3 and a short-term exposure limit (STEL) of 0.02 ppm or 0.14 mg/m3 (10). No exposure limits have been established for 2,6-TDI. This proposed test method has been found satisfactory for measuring 2,4 and 2,6-TDI levels in the workplace.1.1 This test method describes the determination of 2,4-toluene diisocyanate (2,4-TDI) and 2,6-toluene diisocyanate (2,6-TDI) in air samples collected from workplace atmospheres in a cassette containing a glass-fiber filter impregnated with 1-(2-pyridyl)piperazine (1-2 PP). This procedure is very effective for determining the vapor content of atmospheres. Atmospheres containing aerosols may produce low results. 1.2 This test method uses a high-performance liquid chromatograph (HPLC) equipped with a fluorescence or an ultraviolet (UV) detector (1-4). 1.3 The validated range of the test method, as written, is from 1.4 to 5.6 [mu]g of 2,4-TDI and 2,6-TDI which is equivalent to approximately 9.8 to 39 ppb for 2,4-TDI and 2,6-TDI based on a 20-L air sample. The HPLC method using an UV detector is capable of detecting 0.078 [mu]g of 2,4-TDI and 0.068 [mu]g of 2,6-TDI in a 4.0-mL solvent volume, which is equivalent to 0.55 ppb for 2,4-TDI and 0.48 ppb for 2,6-TDI based on a 20-L air sample. 1.4 The isomers of 2,4-TDI, and 2,6-TDI, can be separated utilizing a reversed phase column for the HPLC method. Because industrial applications employ an isomeric mixture of 2,4- and 2,6-TDI, the ability to achieve this separation is important. 1.5 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use. See Section 9 for specific precautions.

Standard Test Method for Determination of 2,4-Toluene Diisocyanate (2,4-TDI) and 2,6-Toluene Diisocyanate (2,6-TDI) in Workplace Atmospheres (1-2 PP Method)

ISO 15202-2:2001 工作场所空气 用感应耦合等离子发射光谱法测定空气中悬浮颗粒物质中的金属和类金属物 第2部分：样品的制备

1 This part of ISO 15202 specifies a number of alternative methods for preparing test solutions from samples of airborne particulate matter collected using the method specified in ISO 15202-1, for subsequent determination of metals and metalloids by ICP-AES using the method specified in ISO 15202-3. NOTE The sample preparation methods described in this part of ISO 15202 are generally suitable for use with analytical techniques other than ICP-AES, e.g. atomic absorption spectrometry (AAS) and inductively coupled plasma mass spectrometry (ICP-MS). 2 The method specified in annex B is applicable when making measurements for comparison with limit values for soluble metal or metalloid compounds. 3 One or more of the sample dissolution methods specified in annexes C through G are applicable when making measurements for comparison with limit values for total metals and metalloids and their compounds. Information on the applicability of individual methods is given in the scope of the annex in which the method is specified. 4 The following is a non-exclusive list of metals and metalloids for which limit values have been set (see reference [1] in the bibliography) and for which one or more of the sample dissolution methods specified in this part of ISO 15202 are applicable. However, there is no information available on the effectiveness of any of the specified sample dissolution methods for those elements in italics. Aluminium Calcium Magnesium Selenium Tungsten Antimony Chromium Manganese Silver Uranium Arsenic Cobalt Mercury Sodium Vanadium Barium Copper Molybdenum Strontium Yttrium Beryllium Hafnium Nickel Tantalum Zinc Bismuth Indium Phosphorus Tellurium Zirconium Boron Iron Platinum Thallium Caesium Lead Potassium Tin Cadmium Lithium Rhodium Titanium ISO 15202 is not applicable to the determination of elemental mercury, since mercury vapour is not collected using the sampling method specified in ISO 15202-1.

Workplace air - Determination of metals and metalloids in airborne particulate matter by inductively coupled plasma atomic emission spectrometry - Part 2: Sample preparation

ANSI Z9.2-2001 局部排气系统设计和操作的指导基本原则

This Standard establishes minimum requirements for the commissioning, design, specification, construction, and installation of fixed industrial local exhaust ventilation (LEV) systems used for the reduction and prevention of employee exposure to harmful airborne substances in the industrial environment.

Fundamentals Governing the Design and Operation of Local Exhaust Systems Copyright Held by AIHA

ISO 15202-1:2000 车间空气 等离子体原子发射光谱法对颗粒物中金属及非金属的测定 第1部分:采样

1 This part of ISO 15202 specifies a method for collecting samples of airborne participate matter for subsequent determination of metals and metalloids using inductively coupled plasma - atomc emission spectrometry. 2 The method is not applicable to the sampling of mercury, which is present in air in the vapour phase at ambient temperatures; inorganic compounds of metals and metalloids that are permanent gases, e.g. arsine (AsH3); or inorganic compounds of metals and metalloids that are present in the vapour phase at ambient temperatures, e.g. arsenic trioxide (As2O3). NOTE Although the method does not describe a means of collecting inorganic compounds of metals and metalloids that are present in the vapour phase, in most instances this is relatively easily achieved by using a back-up filter which has been pre-treated to trap the compound(s) of interest, e.g. a back-up paper pad impregnated with sodium carbonate is suitable for collecting arsenic trioxide (see ISO 11041). 3 The method is applicable to personal sampling of the inhalable or respirable fraction of airborne particles, as defined in ISO 7708, and to static sampling.

Workplace air - Determination of metals and metalloids in airborne particulate matter by inductively coupled plasma atomic emission spectrometry - Part 1: Sampling