NF L52-250-602-2008 Aerospace series - Cables electrical aircraft use - Test methods - Part 602 toxicity 《航空航天系列 航空器用电缆 试验方法 第602部分 毒性》.pdf
《NF L52-250-602-2008 Aerospace series - Cables electrical aircraft use - Test methods - Part 602 toxicity 《航空航天系列 航空器用电缆 试验方法 第602部分 毒性》.pdf》由会员分享,可在线阅读,更多相关《NF L52-250-602-2008 Aerospace series - Cables electrical aircraft use - Test methods - Part 602 toxicity 《航空航天系列 航空器用电缆 试验方法 第602部分 毒性》.pdf(35页珍藏版)》请在麦多课文档分享上搜索。
1、NF EN 3475-602fvrier 2008Ce document est usage exclusif et non collectif des clients Saga Web.Toute mise en rseau, reproduction et rediffusion, sous quelque forme que ce soit,mme partielle, sont strictement interdites.This document is intended for the exclusive and non collective use of Saga Web cus
2、tomers.All network exploitation, reproduction and re-dissemination,even partial, whatever the form (hardcopy or other media), is strictly prohibited.Saga Web Pour SHANGHAI INTERNAT SCIENCE if a specific gas component exists, the indicating layer discolours due to chemical reactions. The length of th
3、e colour change is a measure for the concentration. The concentration of the reactive gases is determined by potentiometry; in this case, electrochemical potentials which can be converted into ppm concentrations after plotting of a calibration curve are measured with ion-specific electrodes in conne
4、ction with a special reference electrode. 5 Preparation for analysis 5.1 General The specimens arranged vertically in a closed test chamber, are chemically decomposed according to EN 3475-601 by thermal radiation alone or in combination with flaming. The resulting smoke portions are optically measur
5、ed according to this test method. In this connection, a gas sample is taken at a time, which has to specified in a test plan. The decomposition gases resulting from thermal degradation are determined qualitatively and quantitatively by means of the analytical procedure described herein. 5.2 Probes f
6、or gas sampling The gases are sampled by means of three probes (internal diameter 6-8 mm) extending into the geometric center of the chamber. EN 3475-602:2007 (F)53.7bouteille dagitation rcipient spcial en verre pour la solution dabsorption 3.8prouvette tube en verre rempli dun ractif spcial destin
7、identifier quantitativement un composant gazeux spcifique 3.9molarit concentration dune solution exprime en nombre de moles (gr/masse molculaire) dun solut par litre de solution 3.10ISA (lonic Strength Adjuster) dispositif de rglage de la force ionique dune solution 3.11NTP (Normal Temperature and P
8、ressure) temprature et pression normales 3.12NBSNational Bureau of Standards, Washington 4 Principe de la mthode Le gaz fumigne produit dans les conditions des essais de densit de fume dcrits dans lEN 3475-601 est sujet analyse en fonction des composants gazeux examiner. La concentration de composan
9、ts gazeux non ractifs est dtermine laide de la procdure colorimtrique. Dans ce cas, on utilise des prouvettes remplies de ractivateur solide ; la couche indicatrice se dcolore par ractions chimiques lorsquelle est en prsence dun composant gazeux spcifique. La longueur du changement de couleur consti
10、tue une mesure de la concentration. La concentration de gaz ractifs est dtermine par potentiomtrie ; dans ce cas, on mesure les potentiels lectrochimiques qui peuvent tre convertis en concentrations ppm aprs avoir trac une courbe dtalonnage laide dlectrodes ioniques spcifiques raccordes une lectrode
11、 de rfrence spciale. 5 Prparation pour lanalyse 5.1 Gnralits Les prouvettes disposes verticalement dans une enceinte dessai ferme sont dcomposes chimiquement selon lEN 3475-601 par radiation thermique seule ou combine avec une flamme vive. Les quantits de fume rsultantes sont mesures optiquement sel
12、on cette mthode dessai. A cet gard, on prlve un chantillon de gaz un moment donn qui doit tre spcifi dans un plan dessai. Les gaz de dcomposition rsultant de la dgradation thermique sont dtermins quantitativement et qualitativement au moyen de la procdure analytique dcrite ici. 5.2 prouvettes pour p
13、rlvement de gaz Les gaz sont prlevs au moyen de trois prouvettes (diamtre interne de 6-8 mm) qui se prolongent dans le centre gomtrique de lenceinte. EN 3475-602:2007 (E) 6Resistant probe materials (such as polypropylene or PTFE) are to be selected due to the reactive behaviour of the halogenides. T
14、he probes are to be connected gastight to the tube fittings for gas sampling at the upper side of the test chamber. Connections not used are to be sealed. One of the probes inserted into the chamber is to be provided with a rubber sleeve for attachment of the test tube for colorimetric “in situ“ mea
15、surement. 5.3 Gas sampling system for non-reactive gases 5.3.1 General Figures 1 and 2 show the basic set-ups for allowable gas sampling systems. 5.3.2 Pipe system for the gas bag A pipe system with a maximum length of 3 m is to be installed between the gas sampling point at the chamber and the plac
16、e of gas collection. If the gas pipe system cannot be heated, thermal insulation of the pipes is to be provided so as to avoid the formation of condensates. The pipes must have an inner width of 6 mm to 8 mm. Plastic hoses or pipes must be used and, depending on the suitability, polyethylene; butadi
17、ene or silicone rubber types can also be used. PTFE are recommended for special requirements with regard to corrosion resistance with temperature load. The gas pipe end facing the chamber is to be provided with a stopcock. 5.3.3 Collection of gases Foil bags with a capacity of 10 l to 15 l and a hig
18、h mechanical and chemical resistance are to be used for the collection of the non-reactive gas components to be analyzed. Polyvinylidene fluoride with low gaseous diffusion and water vapour permeability is recommended as foil material so that a change in the gas composition due to diffusion processe
19、s is negligible: Permeability of gas for O2 max. 20 cm3 NTP/m2 per 24 h N max. 6 cm3 NTP/m2 per 24 h CO2 max. 140 cm3 NTP/m2 per 24 h Water vapour max. 13 g/m2 per 24 h Furthermore, the bags used must be provided with a stopcock. 5.3.4 Gas collection Two approved gas collection processes are availab
20、le, collection by means of vacuum or by suction pump. Vacuum method: A vacuum tank with a minimum capacity of 15 l is recommended for collecting the gas components to be analyzed in the above-stated foil bag. The design of the tank should be 5 l greater then the volume of the bag. The evacuation pre
21、ssure is to be monitored by a vacuum gauge. The vacuum tank is to be provided with a ventilation valve and a connection for the vacuum pump. The tank cover of 10 mm thick acrylic glass minimum is provided with a hole into which a quick-release coupling is to be installed gastight in order to connect
22、 the gas bag, on the one side, with the gas pipe, on the other side. A vacuum pump producing a vacuum in the tank capable of filling a gas bag according to within 20 s is to be used. EN 3475-602:2007 (F)6Choisir des matriaux dprouvette rsistants (comme le polypropylne ou PTFE) en raison du comportem
23、ent ractif des halognides. Les prouvettes doivent tre raccordes aux accessoires du tube et tre tanches aux gaz, en vue de raliser un prlvement de gaz sur le ct suprieur de lenceinte dessai. Les connexions non utilises doivent tre tanchises. Lune des prouvettes introduite dans lenceinte doit tre quip
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