Toimialayhteisöt

 

This document specifies requirements and gives recommendations for next generation sequencing (NGS) workflows. This document covers the pre-examination processes, human DNA (somatic and germline) isolation, sequencing library preparation, sequencing, sequence analysis and reporting of the examination of sequences for diagnostic purposes from isolated DNA from, e.g. formalin-fixed and paraffin embedded tissues, fresh frozen tissues, fine needle aspirates (FNA), whole blood, circulating tumour cells (CTCs), exosomes and other extracellular vesicles, circulating cell free DNA from plasma, and DNA from saliva. NOTE 1 Typical applications include, but are not limited to, NGS for oncology, pharmacogenomics and clinical genetics; approaches include panels (e.g. disease panels, exome panels, target gene panels and in silico panels), exome and whole genome sequencing, as well as certain epigenetics and certain single-cell analyses. This document is addressing in vitro diagnostic examinations including laboratory developed tests and is applicable to medical laboratories, molecular pathology laboratories and molecular genetic laboratories, in vitro diagnostic developers and manufacturers, biobanks as well as institutions and organizations performing biomedical research or sequencing services. This document is not applicable for in situ sequencing, DNA-mediated protein sequencing, forensic sequencing, sequencing of pathogens or microorganisms and microbiome analysis. NOTE 2 International, national or regional regulations or requirements or multiples of them can also apply to specific topics covered in this document.

 

This document specifies requirements and gives recommendations for next generation sequencing (NGS) workflows. This document covers the pre-examination processes, human RNA isolation, sequencing library preparation, sequencing, sequence analysis and reporting of the examination of sequences for diagnostic purposes from isolated RNA from, e.g. formalin-fixed and paraffin embedded tissues, fresh frozen tissues, fine needle aspirates (FNA), whole blood, circulating tumour cells (CTCs), exosomes and other extracellular vesicles, and circulating cell free RNA from plasma. NOTE 1 Typical applications include, but are not limited to, NGS for oncology and clinical genetics, certain single-cell analyses. This document is addressing in vitro diagnostic examinations including laboratory developed tests and is applicable to medical laboratories, molecular pathology laboratories and molecular genetic laboratories, in vitro diagnostic developers and manufacturers, biobanks as well as institutions and organizations performing biomedical research or sequencing services. This document is not applicable for in situ sequencing, forensic sequencing, sequencing of pathogens or microorganisms and microbiome analysis. NOTE 2 International, national or regional regulations or requirements or multiples of them can also apply to specific topics covered in this document.

 

1.1 Scope of EN 1994-1-1 (1) EN 1994-1-1 gives general rules for the design of steel and concrete composite structures and supplementary provisions specific for buildings. NOTE Specific rules for bridges are given in EN 1994-2. 1.2 Assumptions (1) The assumptions of EN 1990-1 apply to EN 1994-1-1. (2) In addition to the general assumptions of EN 1990-1, the assumptions given in EN 1992-1-1, EN 1992-1-2, and EN 1993-1-1 apply to this document. (3) EN 1994-1-1 is intended to be used in conjunction with EN 1990-1, EN 1991 (all parts), EN 1992-1-1, EN 1993 (all parts), EN 1997 (all parts), EN 1998 (all parts when steel and concrete composite structures are built in seismic regions), EN 1090-1, EN 1090-2, EN 1090-4, EN 13670 and ENs for construction products relevant to steel and concrete composite structures.

 

This document specifies the measurement method for the determination of total activity concentration of uranium isotopes in non-saline waters by extraction and liquid scintillation counting. This method covers the measurement of soluble uranium isotopes in water in activity concentrations between approximately 2·10-3 Bq/kg and 10 Bq/kg when analysing a 1 l test sample volume with a 60 000 s counting time with a typical alpha LSC instrument. The ratio 234U/238U can also be determined. This method has not been tested for the measurement of other uranium isotopes.

 

This document specifies a chronic test method for evaluating the habitat function of soils and determining effects of soil contaminants and substances on the reproduction of Hypoaspis (Gaeolaelaps) aculeifer. This method is applicable to soils and soil materials of unknown quality, e.g. from contaminated sites, amended soils, soils after remediation, industrial, agricultural or other sites under concern and waste materials (e.g. dredged material, municipal sludge from a wastewater treatment plant, composed material, or manure, especially those for possible land disposal). This document provides information on how to use this method for testing samples (soils or substances) under temperate conditions. This document is not applicable to substances for which the air/soil partition coefficient is greater than one, or to substances with vapour pressure exceeding 300 Pa at 25 °C. NOTE The stability of the test substance cannot be ensured over the test period. No provision is made in the test method for monitoring the persistence of the substance under test.

 

This document specifies a chronic test method for evaluating the habitat function of soils and determining effects of soil contaminants and substances on the reproduction of Hypoaspis aculeifer by ? mainly ? alimentary uptake. This method is applicable to soils and soil materials of unknown quality, e.g. from contaminated sites, amended soils, soils after remediation, industrial, agricultural or other sites under concern and waste materials (e.g. dredged material, municipal sludge from a wastewater treatment plant, composed material, or manure, especially those for possible land disposal). The reproduction (= number of juveniles) is the measured parameter of the test. The test reflects the bioavailability of a mixture of contaminants in natural soils (contaminated site soils) to a species which represents a trophic level which is not covered by other ISO standards. This test is not intended to replace the earthworm (see ISO 11268-2) or Collembola (see ISO 11267) reproduction tests since this species belongs not only to a different trophic group but also a different taxonomic group (= mites; i.e. arachnids) than those used usually. Effects of substances are assessed using a standard soil, preferably a defined artificial soil substrate. For contaminated soils, the effects are determined in the soil to be tested and in a control soil. Depending on the objective of the study, the control and dilution substrate (dilution series of contaminated soil) are either an uncontaminated soil comparable to the soil to be tested (reference soil) or a standard soil (e.g. artificial soil). This document provides information on how to use this method for testing samples (soils or substances) under temperate conditions. This document is not applicable to substances for which the air/soil partition coefficient is greater than one, or to substances with vapour pressure exceeding 300 Pa at 25 °C. NOTE The stability of the test substance cannot be ensured over the test period. No provision is made in the test method for monitoring the persistence of the substance under test.

 

This document defines technical considerations needed for monitoring unmanned store operations. Technical considerations include the platform, data elements, and interface needed to collect and analyse information from logistics bases, facilities, devices, and other components of unmanned stores. Here, the platform may be designed on a cloud -based system. The Scope Clause 1 is a mandatory element of the text.For rules on the drafting of the Scope, refer to the ISO/IEC Directives, Part 2:2021, Clause 14.

 

Tämä standardi kattaa vaatimukset ja ohjeet uudelleenkäytettävien ontelolaattojen tarkastamiselle, irrottamiselle, kunnostukselle, testaukselle, suunnittelulle ja dokumentoinnille uudelleenkäyttöä varten. Uudelleenkäytettyjä ontelolaattoja käytetään vastaavissa rakenteissa ja käyttökohteissa kuin standardin SFS-EN 1168:2005 + A3:2012 mukaisia uusia ontelolaattoja. Tämän standardin piiriin kuuluvat ekstruuderi- tai liukuvalutekniikalla kertavalulla valmistetut enintään 1200 mm levyiset tai siitä sahaamalla kavennetut ontelolaatat. Standardin piiristä rajataan pois kololaatat. Tämä asiakirja ei määrittele projektikohtaisia yksityiskohtaisia suunnitteluvaatimuksia. Uudelleenkäytettävien ontelolaattojen suunnittelu toteutetaan eurokoodin SFS-EN 1992-1-1:2005 + A1:2015 + AC:2010 ja sen kansallisen liitteen mukaan. Tässä standardissa esitetään, miten saavutetaan eurokoodissa tarvittavat laskentaparametrit ja standardissa SFS-EN 1168:2005 + A3:2012 esitetyt ontelolaattojen oleelliset vaatimukset.

 

This document defines several subsets of the syntax specified in ISO/IEC 21122-1 as profiles. It also defines lower bounds on the throughput in the decoded domain via levels and the encoded domain via sublevels that a conforming decoder implementation shall support. Furthermore, it defines a buffer model to ensure interoperability between implementations in the presence of a latency constraint.

 

Tämä standardi sisältää nestekaasun ja maakaasun käyttölaitteiden ja niihin liitettyjen putkistojen kaavioissa ja piirustuksissa käytettäviksi soveltuvat piirrosmerkit.

 

Standardi esitetään kumottavaksi vanhentuneena  

SFS:n tehtävänä on ylläpitää ajantasaista suomalaista SFS-standardikokoelmaa. 

Tällä lausuntopyynnöllä pyritään selvittämään, tulisiko tämä SFS-standardi kumota vanhentuneena. 

Vastaa kohdassa "Ota kantaa", tulisiko tämä SFS-standardi kumota.  

(Hyväksyn = hyväksyn tämän standardin kumoamisen vanhentuneena.)

 

This document specifies the general requirements for unmanned aircraft docking systems, including the requirements for basic characteristics, functional capabilities, performance criteria, environmental adaptability, electromagnetic compatibility, safety, reliability, maintainability, and testability, as well as the guidelines for marking and packaging. This document applies to the docking systems of civil small multi-copter unmanned aircraft with a maximum take-off mass (MTOM) of level II through level IV as defined in ISO 21895. Docking system supporting other types of unmanned aircraft may also refer to this document. This document does not specify the requirements for vertiports, which are operated under the responsibility of vertiport operators as defined in ISO 5015-2.

 

This document specifies the particular requirements, including performance criteria for washer-disinfectors (WD) that are intended to be used for cleaning and chemical disinfection of thermolabile endoscopes. This document also specifies the performance requirements for the cleaning and disinfection of the WD and its components and accessories which can be required to achieve the necessary performance criteria. The methods, instrumentation and instructions required for type testing, works testing, validation (installation, operational and performance qualification on first installation), routine control and monitoring, and requalification of WD periodically and after essential repairs, are also specified. NOTE 1 In addition, Annex A gives guidance on an appropriate division of responsibility for the range of activities covered by this document. NOTE 2 WD conforming with this document can also be used for cleaning and chemical disinfection of other thermolabile re-usable medical devices for which the device manufacturer has recommended and validated this method of disinfection. WD conforming with the requirements of this document are not intended for cleaning and disinfection of medical devices, including endoscopic accessories, which are heat stable and can be disinfected or sterilized by thermal methods (see ISO 15883-1:2024, 4.1.5). NOTE 3 The specified performance requirements of this document cannot ensure the inactivation or removal of the causative agent(s) (prion protein) of transmissible spongiform encephalopathies. NOTE 4 If it is considered that prion protein might be present, particular care is needed in the choice of cleaning agents and disinfectants to ensure that the chemicals used do not react with the prion protein or other protein in a manner that can inhibit its removal or inactivation from the load or WD. NOTE 5 This document can be used by prospective purchasers and manufacturers as the basis of agreement on the specification of the WD, manufacturers of endoscopes, cleaning products, and disinfecting products.

 

This specification defines the Trusted Platform Module (TPM) a device that enables trust in computing platforms in general. It is broken into parts to make the role of each part clear. All parts are required in order to constitute a complete standard.

 

For a complete definition of all requirements necessary to build a TPM, the designer will need to use the appropriate platform-specific specification to understand all of the requirements for a TPM in a specific application or make appropriate choices as an implementer.

 

Those wishing to create a TPM need to be aware that this specification does not provide a complete picture of the options and commands necessary to implement a TPM. To implement a TPM the designer needs to refer to the relevant platform-specific specification to understand the options and settings required for a TPM in a specific type of platform or make appropriate choices as an implementer.

 

The number of platform configuration registers and their attributes are not defined in this specification. Those values would be specified by a platform specific specification or alternatively determined by an implementer. 

 

This part of the Trusted Platform Module Library specification contains the definitions of the constants, flags, structure, and union definitions used to communicate with the TPM. Values defined in this document are used by the TPM commands defined in ISO/IEC 11889 Part 3: Commands and by the functions in the Reference Code.

 

NOTE The structures in this document are the canonical form of the structures on the interface. All structures are “packed” with no octets of padding between structure elements. The TPM-internal form of the structures is dependent on the processor and compiler for the TPM implementation.

 

This ISO/IEC 11889 Part 3 of the Trusted Platform Module Library specification contains the definitions of the TPM commands. These commands make use of the constants, flags, structures, and union definitions defined in ISO/IEC 11889 Part 2.

 

The combination of this ISO/IEC 11889 Part 3 and the Reference Code is sufficient to fully describe the required behavior of a TPM. The Reference Code is written to define the behavior of a compliant TPM. In some cases (e.g., firmware update), it is not practical to require a single compliant implementation. In those cases, any implementation provided by the vendor that meets the general description of the function provided in ISO/IEC 11889 Part 3 would be compliant.

 

The Reference Code is not written to meet any particular level of conformance nor does this specification require that a TPM meet any particular level of conformance.

 

This document defines terms and expressions used in the field of underwater bioacoustics and biotremology, including sound production by aquatic life (including all life forms that use aquatic habitats), reception of sound by aquatic life, effects of sound on aquatic life, scattering of sound from aquatic life, passive and active acoustic monitoring of aquatic life, and sound mapping.

 

This document specifies the complete specification operator for surface texture (scale-limited surfaces) by areal methods.

 

This document defines technical concepts for unmanned stores and classifies them according to the degree of autonomy in their operations and/or services. It includes a definition, relevant actors, and a classification of unmanned stores. It also outlines the detailed operations and services by autonomy level, including those at unmanned stores.

 

This document describes a gas chromatographic method for determination of 5 chlorophenols (2-chlorophenol; 2,4-dichlorophenol; 2,4,6-trichlorophenol; 2,3,4,6-tetrachlorophenol; pentachlorophenol) in water samples. This method uses a liquid/solid extraction method using immersive solid phase extraction equipment. After sampling, retained organic compounds are released by thermal desorption (TD) and automatically transferred to a gas chromatography-mass spectrometry (GC-MS) system for analysis. NOTE 1 Other chlorophenols not specified in the scope can also be analysed if the performance specifications of this method can be met and the user validates the changes of the procedure accordingly. NOTE 2 The method detection limits (MDLs) of each chlorophenol measured by this method are shown in Annex B. This method is applicable to the determination of chlorophenols in surface water, ground water and drinking water. The applicability of the method to other types of water can be validated by the user separately for each individual case.