Toimialayhteisöt

 

This document covers the design of PE and PP flexible packaging with respect to compatibility of the design with recycling processes available for PE and PP packaging. Packaging constituents and components used in/on PE and PP flexible packaging but made of materials other than PE and PP are also covered by this document as these need to be evaluated for compatibility with PE and PP mechanical recycling processes.

 

This document covers the design of PE and PP rigid with respect to compatibility of the design with recycling processes. Packaging constituents and packaging components made of other materials than PE and PP are also covered by this document as they need to be evaluated on compatibility with polymer recycling.

 

This document specifies methods for the determination of diameter and length of pellets. Concerning the pellet length methods for the determination of fractions of specified length, such as oversized particles and particles below 10 mm and for determination of the average length are included.

 

This document specifies a process to design, implement, maintain and monitor BNG outcomes through the lifecycle of spatially explicit development projects and until the expected outcome on biodiversity has been realized. It does not cover the detailed requirements associated with the delivery of biodiversity enhancements or management. It provides a framework to demonstrate that a project has followed a process that is based on The BBOP Principles on Biodiversity Offsets and aligns with the vision, goals and targets of the Convention on Biological Diversity and the Global Biodiversity Framework. Complying with the requirements within this document is to follow a process to achieve BNG that is based on good practice. This document is for any sector of industry, including residential, mixed-use, energy, water, extractive industry, transport, communications agriculture, forestry and infrastructure. It is for any scale of project from individual house-builds to larger developments and will be of use by anybody involved in development including ecologists, planners, biologists, auditors, developers, conservation organisations, land managers, planning authorities and organisations and investors. It can also be used by land managers aiming to generate BNG through management of their land. Hereafter the term “project” refers to both development projects and land management activities. This document covers terrestrial and freshwater habitats, and intertidal habitats down to the mean low water mark as the process and methods to deliver net gain for marine habitats are different from the approach set out here. This document is applicable for projects that affect biodiversity and those with limited or no impact on biodiversity, as well as projects aiming to achieve BNG on- and/ or off-site. It first sets out requirements that apply throughout the BNG process; these requirements are in Clause 5. Clause 6 to Clause 9 contain requirements for each of these stages of the BNG process: A project may involve requirements to achieve BNG from, for example, a planning requirement or compliance with legislation. This document covers a process to achieve BNG, notwithstanding any such requirements. It does not infer compliance with any planning condition, legislation or statutory requirement, and is independent from any mandatory or legislative requirement for BNG. Furthermore, following the BNG process in this document does not substitute the requirements to assess ecological beneficial and adverse impacts and report them, e.g., as part of an Environmental Impact Assessment (EIA). Rather, this document builds on, and is not intended to repeat, existing good practice for biodiversity surveys, impact assessments, mitigation and compensation for projects. Projects with adverse impacts on irreplaceable biodiversity features, such as irreplaceable habitats cannot achieve BNG. These projects can follow the process in this document for biodiversity features that are not irreplaceable but cannot claim project-wide achievement of BNG. These projects need to transparently and comprehensively refer to the adverse impacts on irreplaceable biodiversity features in communications and reports. Projects that will impact irreplaceable biodiversity features areas should be actively avoided.

 

This document specifies a test method for determining the screen touch property of the textiles. The method is applicable to all types of fabrics which are intended to be used for products that could handle the screen.

 

ISO 11609:2017 specifies requirements for the physical and chemical properties of dentifrices and provides guidelines for suitable test methods. It also specifies requirements for the marking, labelling and packaging of dentifrices. ISO 11609:2017 applies to dentifrices, including toothpastes, destined to be used by the consumers on a daily basis with a toothbrush to promote oral hygiene. Specific qualitative and quantitative requirements for freedom from biological and toxicological hazards are not included in this document. These are covered in ISO 7405[1] and ISO 10993-1[2].

 

This document establishes general requirements for the application of fracture control technology to fracture-critical items (FCIs) fabricated from metallic, non-metallic or composite materials. It also establishes mechanical damage control requirements for mechanical-damage-critical items (MDCIs) fabricated from composite materials. These requirements, when implemented on a particular space system, can assure a high level of confidence in achieving safe operation and mission success. The requirements set forth in this document are the minimum fracture control and mechanical damage control requirements for FCIs and MDCIs in general space systems, including launch vehicles, spacecraft and ground support equipment. With necessary modifications, these requirements may also be applicable to reusable launch vehicles (RLVs). This document is not applicable to the Shuttle and its payloads or the ISS and its equipment, since they already have a set of specific requirements suitable for their special applications. This document is not applicable to processing detected defects.

 

This part of ISO 13347 deals with the determination of the acoustic performance of fans. In addition, it may be used to determine the acoustic performance of fans combined with an ancillary device such as a roof cowl or damper or, where the fan is fitted with a silencer, the sound power resulting from the fan and silencer combination.

 

This part of ISO 13347 gives a detailed description of reverberant room methods for the determination of fan sound power levels. It is for use under standardized laboratory conditions and recognises that tests in situ are subject to increased uncertainty. These test procedures are not necessarily appropriate to site test conditions. Acoustic system effects are presently the subject of considerable research effort. ISO 5136, which covers the in-duct method, and ISO 10302-1 for small fans, should be used in conjunction with this part of ISO 13347.

 

This part of ISO 13347 applies to fans as defined in ISO 5801 and ISO 13349-1. It is limited to the determination of airborne sound emission for the specified installation categories. Vibration is not measured, nor is the sensitivity of airborne sound emission to vibration effects determined. The sizes of the fan, which can be tested in accordance with this part of ISO 13347, are limited only by the practical aspects of the test installations. This part of ISO 13347 determines sound power by using sound intensity measurements on a measurement surface which encloses the sound source. It provides guidelines on the acoustical environment, ambient noise, measurement surface, and number of measurements. The installation categories are generally designed to represent the physical orientation of a fan installed in accordance with ISO 5801, ISO 13350 and also defined in ISO 13349-1.

 

This document specifies the procedure for a quantitative determination of major and trace element concentrations in homogeneous solid waste, soil, soil-like material and sludge by energy dispersive X-ray fluorescence (EDXRF) spectrometry or wavelength dispersive X-ray fluorescence (WDXRF) spectrometry using a calibration with matrix-matched standards. This document is applicable for the following elements: Na, Mg, Al, Si, P, S, Cl, K, Ca, Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Zn, As, Se, Br, Rb, Sr, Y, Zr, Nb, Mo, Ag, Cd, Sn, Sb, Te, I, Cs, Ba, Ta, W, Hg, Tl, Pb, Bi, Th and U. Concentration levels between approximately 0,000 1 % and 100 % can be determined depending on the element and the instrument used.

 

This document defines terms used in digital imaging.

 

This part of ISO/IEC 30108 defines biometric services used for identity assurance that are invoked over a services-based framework. It provides a generic set of biometric and identity-related functions and associated data definitions to allow remote access to biometric services. The binding of these services to specific frameworks is not included in this document, but is the subject of other parts of the ISO/IEC 30108 series. Although focused on biometrics, this standard includes support for other related identity assurance mechanisms such as biographic and document capabilities. IAVS is intended to be compatible with and used in conjunction with other biometric standards as described in Clause 3. Specification of biometric functionality is limited to remote (backend) services. Services between a client-side application and biometric capture devices are not within the scope of this standard. Integration of biometric services as part of an authentication service or protocol is not within the scope of this standard.

 

This part of ISO 5725 describes the use of robust methods for analysing the results of precision experiments without using outlier tests to exclude data from the calculations, and in particular, the detailed use of several such methods. The robust methods described in this document allow the data to be analysed in such a way that it is not required to make decisions about outliers that affect the results of the calculations.

 

This document deals with the assessment of human exposure from ingestion of soil. It specifies a simplified method for the estimation of the oral bioaccessibility of metal(loid)s from contaminated soils. The method is a chemical extraction using hydrochloric acid (HCl) and can be used at least as a first-tier screening to predict the oral bioaccessibility of arsenic (As), cadmium (Cd) and lead (Pb) in soil samples. It produces extracts that are representative of the bioaccessible concentrations measured by using the validated UBM (unified bioaccessibility method) test (ISO 17924)[1]. Soils, in sieved form (fraction < 250 µm without prior mechanical grinding) as recommended in ISO 17924, are extracted in an environment that simulate very simply the acidic conditions of the gastric compartment. This document describes the protocol and the approach to calculate the oral bioaccessibility of As, Cd and Pb in soils, usually measured with ISO 17924. From the extractable concentrations of metal(loid)s by HCl, the predicted bioaccessibility in both the gastric and gastrointestinal phases is calculated by taking the equations from simple linear regressions. In a second-tier study and a complementary validation approach, the ISO 17924 protocol is applicable to selected soil samples (approximately 10 % of samples) for better assessment of human exposure.

 

 

 

This document specifies requirements for electroplated coatings of zinc with supplementary treatments using hexavalent chromium compounds on iron or steel. It includes information to be supplied by the purchaser to the electroplater, and the requirements for heat treatment before and after electroplating. It is not applicable to zinc coatings applied This document does not specify requirements for the surface condition of the basis metal prior to electroplating with zinc. However, defects in the surface of the basis metal can adversely affect the appearance and performance of the coating. The coating thickness that can be applied to threaded components can be limited by dimensional requirements, including class or fit.

 

ISO 2081:2018 specifies requirements for electroplated coatings of zinc with supplementary treatments on iron or steel. It includes information to be supplied by the purchaser to the electroplater, and the requirements for heat treatment before and after electroplating. ISO 2081:2018 is not applicable to zinc coatings applied - to sheet, strip or wire in the non-fabricated form, - to close-coiled springs, or - for purposes other than protective or decorative. ISO 2081:2018 does not specify requirements for the surface condition of the basis metal prior to electroplating with zinc. However, defects in the surface of the basis metal can adversely affect the appearance and performance of the coating. The coating thickness that can be applied to threaded components can be limited by dimensional requirements, including class or fit.

 

This document specifies the procedure for a quantitative determination of major and trace element concentrations in homogeneous solid waste, soil, soil-like material and sludge by energy dispersive X-ray fluorescence (EDXRF) spectrometry or wavelength dispersive X-ray fluorescence (WDXRF) spectrometry using a calibration with matrix-matched standards. This document is applicable for the following elements: Na, Mg, Al, Si, P, S, Cl, K, Ca, Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Zn, As, Se, Br, Rb, Sr, Y, Zr, Nb, Mo, Ag, Cd, Sn, Sb, Te, I, Cs, Ba, Ta, W, Hg, Tl, Pb, Bi, Th and U. Concentration levels between approximately 0,000 1 % and 100 % can be determined depending on the element and the instrument used.