13.030.30 特殊废物 标准查询与下载

GSO ISO 7760:2015 摄影 制造过程废物 对苯二酚测定

This International Standard specifies a spectrophotometric method for the determination of hydroquinone in photographic processing waste. This method can be applied to samples containing hydroquinone in the concentration range of 200 μg/l to 4 000 μg/l; aminophenols and phenylenediamines should also be determined by this method. However, sulfonated hydroquinones or products from the further oxidation of benzoquinone will not be determined.

Photography -- Processing waste -- Determination of hydroquinone

GSO ISO 6849:2015 摄影 制造过程废物 硼测定

This International Standard specifies two methods for the determination of boron in photographic processing wastes. The first method is the estimation of borates by titration of the boric acid-mannitol complex, which is a stronger acid than the boric acid from which it is formed. It is suitable for boron concentrations of 0,1 mg/l and higher. In the range 0,1 mg/l to 5 mg/l, phosphate is removed by precipitation by lead acetate. In the range 1 mg/l to 100 mg/l, the sample is diluted 25 times; this eliminates phosphorous interference if the phosphorous concentration is below 500 mg/l. The second and alternative method is a spectrophotometric technique using methylene blue and is useful in the boron range of 0,1 ml/l to 1,0 mg/l, this being the concentration likely to be encountered in photographic processing wastes.

Photography -- Processing wastes -- Determination of boron

GSO ISO 6853:2015 摄影 -废物处理 -铵态氮的测定（微扩散法）

This International Standard specifies a method for the determination of ammonia and other volatile amines that can be liberated from photographic processing wastes by strong alkali, the results being expressed in terms of nitrogen. The method is applicable for the determination of the ammonia concentration of typical photoprocessing wastes in the range of 10 mg/l to 200 mg/l of ammonia or 8 mg/l to 160 mg/l of nitrogen. Other volatile amines are determined as ammonia, but their concentrations in photoprocessing wastes are usually very low.

Photography -- Processing waste -- Determination of ammoniacal nitrogen (microdiffusion method)

NF X30-511:2015 医疗废物包装 锐器容器的附加和/或替代特性和要求

Packaging for medical care waste - Additional and/or alternative characteristics and requirements for sharps containers

ASTM F1737/F1737M-15 在溢出期间使用溢油分散剂应用设备的标准指南: 喷杆和喷嘴系统

3.1 This guide provides information, procedures, and requirements for management and operation of dispersant spray application equipment (boom and nozzle systems) in oil spill response. 3.2 This guide provides information on requirements for storage and maintenance of dispersant spray equipment and associated materials. 3.3 This guide will aid operators in ensuring that a dispersant spray operation is carried out in an effective manner. 1.1 This guide covers considerations for the maintenance, storage, and use of oil spill dispersant application systems. 1.2 This guide is applicable to spray systems employing booms and nozzles and not to other systems such as fire monitors or single-point spray systems. 1.3 This guide is applicable to systems employed on ships or boats and helicopters or airplanes. 1.4 This guide is applicable to temperate weather conditions and may not be applicable to freezing conditions. 1.5 This guide is one of five related to dispersant application systems. Guide F1413/F1413M covers design, Practice F1460/F1460M covers calibration, Test Method F1738 covers deposition, Guide F1737 covers the use of the systems, and Guide F2465/F2465M covers the design and specification for single-point spray systems. Familiarity with all five standards is recommended. 1.6 The values stated in either SI units or inch-pound units are to be regarded separately as standard. The values stated in each system may not be exact equivalents; therefore, each system shall be used independently of the other. Combining values from the two systems may result in non-conformance with the standard. 1.7 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.

Standard Guide for Use of Oil Spill Dispersant Application Equipment During Spill Response: Boom and Nozzle Systems

ASTM D4447-15 处理实验室化学品和样品的标准指南

4.1 “Stand-alone” laboratories rarely generate or handle large volumes of hazardous substances. However, the safe handling and disposal of these substances is still a matter of concern. Since the promulgation of the Resource Conservation and Recovery Act (RCRA) of 1976, more attention has been given to the proper handling and disposal of such materials. States may adopt more stringent requirements; information on this may be found along the path EPA Home > Wastes > Regions/States/Tribes > RCRA State Authorization > Data, Charts and Graphs (STATS) > State/Regional. To keep track of this, EPA classifies state regulatory language as (1) authorized, (2) procedural/enforcement, (3) broader in scope, and (4) unauthorized, and it publishes notices concerning the first three in the Federal Register. 4.2 Laboratory management should designate an individual who will be responsible for waste disposal and must review the RCRA guidelines, in particular: 40 CFR 261.3 - definition of a hazardous waste, 40 CFR 261.33 -specific substances listed as hazardous, 40 CFR 262 - generator requirements and exclusions, and proper shipping and manifesting procedures. 4.3 Because many laboratory employees could be involved in the proper treatment and disposal of laboratory chemicals and samples, it is recommended that a safety and training program be designed and presented to all regarding procedures to follow in the treatment and disposal of designated laboratory wastes. This recommendation is required in the United States by the EPA (40 CFR 265.16). For those who pack and ship, Hazardous Materials Shipper training is also required by DOT (49 CFR 172.203).5 4.4 If practical and economically feasible, it is recommended that all laboratory waste be either recovered, re-used, or disposed of in-house. However, should this not be the case, other alternatives are presented. This guide is intended only as a suggested organized method for classification, segregation, and disposal of chemical laboratory waste. A university can set up its own chemical distributor to take orders from departments, order in economical quantities, sell at prorated bulk price plus expenses, and take back what is unused. For an example of a university central facility for minimizing over-ordering, storing chemical packages between uses, and disposing of hazardous wastes, see the web site of the University of Vermont, especially Procedure 12: Laboratory Waste Pickup and RCRA Hazardous Waste Determination. 4.5 The handling of laboratory samples, especially those received in large numbers or quantities from a specific source, can often be accommodated by returning the material to the originator, for processing and potentially combining with larger quantities of the same material for recycling or disposal. Shipments of hazardous waste, including samples, are subject to RCRA regulations that do not apply to shipments of what is similar but not waste-like. A sample that was not a waste as received, and has not been contaminated or ......

Standard Guide for Disposal of Laboratory Chemicals and Samples

DB22/T 2189-2014 医疗废物管理规范

Medical Waste Management Regulations

DB31/ 829-2014 医疗废物转运技术及作业要求

本标准规定了上海市医疗废物转运的技术要求、操作作业规程和管理要求。 本标准适用于上海市医疗废物转运过程中的操作与管理。

Medical waste transfer technology and operation requirements

DB21/T 2330-2014 含有“瘦肉精”的动物及动物产品无害化处理技术规范

Technical Specifications for the Harmless Treatment of Animals and Animal Products Containing "Clenbuterol"

ASTM D5659-14 使用高效液相色谱法的废水中氯苯氧基酸除草剂的标准试验方法

4.1 Phenoxy acid herbicides are used extensively for weed control. Esters and salts of 2,4-D, 2,4,5-T, and Silvex have been used for agricultural crop and lawn care. 1.1 This test method covers the analysis of 2,4-dichlorophenoxyacetic acid (2,4-D), 2,4,5-trichlorophenoxyacetic acid (2,4,5-T), and 2,4,5-trichlorophenoxypropionic acid (silvex) in liquids and solids, using high performance liquid chromatography with an ultraviolet detector (HPLC/UV). This test method is applicable for a concentration range from approximately 50 to 1000 ppm. This range takes into consideration the sample preparation and dilutions outlined in Section 10. Lower detection levels can be obtained by using larger sample sizes, smaller total final volumes, or with the use of in-line or solid phase extraction, concentration, or cleanup, or combinations thereof. 1.2 The chlorophenoxy herbicides may be present as a variety of salts or esters, which are converted to, analyzed, and reported as their respective acids. 1.3 This test method is applicable to liquid and solid waste and waste extract matrices including aqueous, oil, spent solvent, soil, ash, leachates, etc. 1.4 This test method may be applicable to other phenoxy acid herbicides. 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 7 and 10.3.1 for specific precautionary statements.

Standard Test Method for Chlorophenoxy Acid Herbicides in Waste Using HPLC

GSO ISO 10348:2013 照相加工废物银含量的测定

This International Standard gives methods for determining the silver content in photographic effluents from photographic processing wastes. Sampling, sample preservation and analytical methodology are included. Three analytical procedures are given with two supporting sample treatment methodologies: a) a flame atomic absorption spectroscopy (AAS) method; b) two Potentiometrie iodide titration (PT) methods. The choice of treatment is dependent on the analysis method and form of sample. Where AAS is the chosen method for analysis, cyanogen iodide-treated or preserved samples may be analysed directly. For the PT method, two digestion procedures are given: Digestion A for effluents with low salt content, and Digestion B for samples with high solids content.

Photography -- Processing wastes -- Determination of silver content

ANSI N13.45-2012 低强度放射性废物的焚化

Provides guidelines for incineration of combustible forms of low-level radioactive waste. It addresses the siting, licensing and permitting, operation and monitoring of the incinerator operation, disposal of residues, and decommissioning. This standard may be applied to incineration of mixed wastes, i.e., radioactive wastes that contain other hazardous components as defined by federal or state agencies, provided consideration is given to additional design features and regulatory permitting required by the hazardous nature of the wastes.

Incineration of Low-Level Radioactive Waste

NF X30-500:2011 医疗废物的包装.穿孔废物箱和小型收集器的规定和测试.

Packaging for medicinal care waste - Boxes and small collectors for perforating waste - Specifications and tests.

DS/CEN/TS 16229:2011 废弃物的表征 排放到尾矿池的弱酸可离解氰化物的取样和分析

This CEN Technical Specification specifies methods for sampling and analysis of weak acid dissociable cyanide discharged into tailings ponds. NOTE The document can be used to support the requirements in the Directive 2006/21/EC of the European Parliament and of the Council of 15 March 2006 on the management of waste from extractive industries.

Characterization of waste - Sampling and analysis of weak acid dissociable cyanide discharged into tailings ponds

ISO/FDIS 24544:2011 稀土-可回收的钕铁硼(NdFeB)资源-分类、一般要求和验收条件

Rare earth – Recyclable Neodymium iron boron (NdFeB) resources - Classification, general requirements and acceptance conditions

ASTM C1751-11 放射性废料槽取样的标准指南

Obtaining samples of high-level waste created during the reprocessing of spent nuclear fuels presents unique challenges. Generally, high-level waste is stored in tanks with limited access to decrease the potential for radiation exposure to personnel. Samples must be obtained remotely because of the high radiation dose from the bulk material and the samples; samples require shielding nbsp;nbsp;nbsp;for handling, transport, and storage. The quantity of sample that can be obtained and transported is nbsp;nbsp;nbsp;small due to the hazardous nature of the samples as well as their high radiation dose. Many high-level wastes have been treated to remove strontium (Sr) or cesium (Cs), or both, underwent liquid volume reductions through forced evaporation or have been pH modified, or both, to decrease corrosion of the tanks. These processes, as well as waste streams added from multiple process plant operations, often resulted in precipitation, and produced multiphase wastes that are heterogeneous. Evaporation of water from waste with significant dissolved salts concentrations has occurred in some tanks due to the high heat load associated with the high-level waste and by intentional evaporative processing, resulting in the formation of a saltcake or crusts, or both. Organic layers exist in some waste tanks, creating additional heterogeneity in the wastes. Due to these extraordinary challenges, substantial effort in research and development has been expended to develop techniques to provide grab samples of the contents of the high-level waste tanks. A summary of the primary techniques used to obtain samples from high-level waste tanks is provided in Table 1. These techniques will be summarized in this guideline with the assumption that the tank headspace is adequately ventilated during sampling. TABLE 1 High-Level Waste Tank Sampling Methods TechniqueMaterial TypeNotes SolidSlurryLiquid HAST in-tank needle orifice X Orifice as part of Reverse-Flow Diverter (RFD) Bottle on a String X X Dip sample Vacuum Pump X X Auger X X Only high viscosity slurries Sample Cup X X Manual system used at Savannah River Site to obtain salt-cake samples and hard sludges that don’t slump. Core Drilling Rotary Mode (Hanford Sampler) X X

Standard Guide for Sampling Radioactive Tank Waste

ASTM C1750-11 仿真高强度灌装(放射性)废料的开发,验证,批准和建档标准指南

1.1 Intent: 1.1.1 The intent of this guideline is to provide general considerations for the development, verification, validation, and documentation of high-level waste (HLW) tank simulants. Due to the expense and hazards associated with obtaining and working with actual wastes, especially radioactive wastes, simulants are used in a wide variety of applications including process and equipment development and testing, equipment acceptance testing, and plant commissioning. This standard guide facilitates a consistent methodology for development, preparation, verification, validation, and documentation of waste simulants. 1.2 This guideline provides direction on (1) defining simulant use, (2) defining simulant-design requirements, (3) developing a simulant preparation procedure, (4) verifying and validating that the simulant meets design requirements, and (5) documenting simulant-development activities and simulant preparation procedures. 1.3 Applicability: 1.3.1 This guide is intended for persons and organizations tasked with developing HLW simulants to mimic certain characteristics and properties of actual wastes. The process for simulant development, verification, validation, and documentation is shown schematically in Fig. 1. Specific approval requirements for the simulants developed under this guideline are not provided. This topic is left to the performing organization. 1.3.2 While this guide is directed at HLW simulants, much of the guidance may also be applicable to other aqueous based solutions and slurries. 1.3.3 The values stated in SI units are to be regarded as the standard. The values given in parentheses are for information only. 1.4 User Caveats: 1.4.1 This guideline is not a substitute for sound chemistry and chemical engineering skills, proven practices and experience. It is not intended to be prescriptive but rather to provide considerations for the development and use of waste simulants. 1.4.2 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. FIG. 1 Simulant Development, Verification, Validation, and Documentation Flowsheet

Standard Guide for Development, Verification, Validation, and Documentation of Simulated High-Level Tank Waste

ASTM E1368-11 目检石棉拆除工程的标准操作规程

This practice applies to response actions for all types of asbestos-containing materials, including surfacing materials, thermal systems insulation, and miscellaneous materials, whether friable or not, regardless of the quantities involved and the reason for conducting the response action. Abatement for the purpose of removing asbestos-containing materials or encapsulating or enclosing them, regardless of the engineering controls and work practices used, requires performance of visual inspections as described in this practice. Operations and maintenance (O&M) activities, such as removal, encapsulation, or enclosure of asbestos-containing materials incidental to repair or replacement of a component, clean-up of debris from a fiber release episode, or other preventive measures, require the performance of visual inspections as described in this practice. See Managing Asbestos in Place and Guidance Manual. This practice applies to response actions performed under a contract from the building owner, as well as to work performed by the building owner''s staff. The specific objectives of the visual inspection process before, during, and at the conclusion of an asbestos abatement project are: to review the extent of asbestos-containing material (ACM) within the scope of work, to monitor performance of the work, and to verify if visible residue, dust or debris, or unremoved material are absent at the completion of removal and clean-up activities. The visual inspection process is used to evaluate all four aspects of an asbestos abatement project as follows: Extent of ACM within Scope of Work8212;The building survey which is intended to locate and quantify asbestos-containing materials is not properly called a “visual inspection” within the context of this practice. To define the extent of ACM involved, a building survey is a necessary prelude to the first step of the visual inspection process. The building survey, which may use other building records, is intended to locate and assess the condition of ACM with confirmation by laboratory analysis of bulk samples. Additional surveys may be required during project design to find ACM in locations not entered or accessible during the initial building survey. The extent of the ACM to be abated must be known in order to properly design the abatement project. See 40 CFR Part 61. Project Work Performance8212;Observation of work activities throughout the abatement project confirms acceptable work performance and aids the visual inspection for completeness of removal of ACM from the surfaces and components and for completeness of cleanup of the work area. Careful examination of the work area may be required at the start of the project for debris that may have been generated after the building surveys and project design. Completeness of Abatement8212;The presence of residue, visible without the use of magnifying devices, on surfaces and components from which asbestos has been removed indicates that additional cleaning of these surfaces is required. All ACM required to be removed by the contract documents must be gone in order to pass the inspection for completeness of removal. Similarly, the presence of improperly encapsulated or insufficiently enclosed material indicates that these measures, if used for abatement or as an adjunct thereto, were inadequately performed and corrective action shall be taken. Completeness of Clean-up8212;The presence of dust or debris on surfaces in areas where abatement has taken place indicates that......

Standard Practice for Visual Inspection of Asbestos Abatement Projects

NF X30-502:2010 医疗保健废弃物的封装.牙科汞齐废弃物封装.试验和规范.

Packaging for medical care waste - Dental amalgam waste packaging - Tests and specifications.

GSO ASTM E1368:2010 石棉减排项目虚拟检查的标准实施规程

1.1 This practice covers procedures for performing visual inspections of asbestos response actions to: 1.1.1 Establish the extent of the required work before it begins; 1.1.2 Determine the progress and quality of the work and evaluate the completeness of the response action; and 1.1.3 Evaluate the cleanliness of the work area prior to final air testing for clearance (if performed), and subsequent to dismantling of critical barriers. 1.2 This practice can be used on an abatement project, or for operations and maintenance (O&M) work, performed by the building owner’s staff. It can also be used in conjunction with contract documents between the building owner and other parties involved in an abatement project. NOTE 1—Standard contract documents (such as AIA and EJCDC documents) define contractual relationships and responsibilities for projects within the construction industry. Asbestos abatement projects differ from traditional construction projects in the manner of their design and execution, as well as in the type and level of oversight required to substantiate their successful completion. Non-traditional responsibilities are given to the building owner, project designer, and abatement contractor by this practice. Furthermore, responsibilities related to project oversight, inspections, and approvals are placed upon an additional non-traditional representative of the building owner; the project monitor, as defined by this practice. All parties are cautioned that the subject authorities and corresponding responsibilities be understood, mutually agreed upon, and correspondingly addressed with appropriate modifications, if necessary, to the contract documents for a specific project. 1.3 This practice provides the following information: 1.3.1 The objectives of the visual inspection process; 1.3.2 The responsibilities and qualifications of the individuals involved in the visual inspections; 1.3.3 The schedule of visual inspection activities during an abatement project and O&M work; 1.3.4 The inspection procedures for the various types of abatement work and O&M tasks; and 1.3.5 The criteria for certifying work as complete on the basis of the visual inspections. 1.4 The values stated in inch-pound units are to be regarded as standard. The values given in parentheses are mathematical conversions to SI units that are provided for information only and are not considered standard. 1.5 Warning—Asbestos fibers are acknowledged carcinogens. Breathing asbestos fibers can result in disease of the lungs including asbestosis, lung cancer, and mesothelioma. Precautions in this standard practice should be taken to avoid creating and breathing airborne asbestos particles from materials known or suspected to contain asbestos. See 2.2 for regulatory requirements addressing asbestos. 1.6 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 safety statements, see 12.2.

Standard Practice for Visual Inspection of Asbestos Abatement Projects