ASTM D4984-2006(2011) Standard Test Method for Carbon Dioxide in Natural Gas Using Length-of-Stain Detector Tubes 《使用着色长度检测管对天然气中的二氧化碳的标准试验方法》.pdf

《ASTM D4984-2006(2011) Standard Test Method for Carbon Dioxide in Natural Gas Using Length-of-Stain Detector Tubes 《使用着色长度检测管对天然气中的二氧化碳的标准试验方法》.pdf》由会员分享，可在线阅读，更多相关《ASTM D4984-2006(2011) Standard Test Method for Carbon Dioxide in Natural Gas Using Length-of-Stain Detector Tubes 《使用着色长度检测管对天然气中的二氧化碳的标准试验方法》.pdf（3页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: D4984 06 (Reapproved 2011)Standard Test Method forCarbon Dioxide in Natural Gas Using Length-of-StainDetector Tubes1This standard is issued under the fixed designation D4984; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revis

2、ion, the year of last revision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon () indicates an editorial change since the last revision or reapproval.1. Scope1.1 This test method covers a rapid and simple field deter-mination of carbon dioxide in natural gas pipe

3、lines. Availabledetector tubes provide a total measuring range of 100 ppm(parts per million) up to 60 % by volume, although the majorityof applications will be on the lower end of this range (that is,under 5 %).At least one manufacturer provides a special kit formeasurements from 10 to 100 % CO2, bu

4、t the normal 100-cchand pump is not used. See Note 1.NOTE 1High-range carbon dioxide detector tubes will have measur-ing ranges in percent (%) CO2, and low-range tubes will be in parts permillion (ppm). To convert percent to ppm, multiply by 10 000(1%=10000ppm).1.2 The values stated in SI units are

5、regarded as standard.The inch-pound units in parentheses are for information only.1.3 This standard does not purport to address all of thesafety concerns, if any, associated with its use. It is theresponsibility of the user of this standard to establish appro-priate safety and health practices and d

6、etermine the applica-bility of regulatory limitations prior to use.2. Referenced Documents2.1 Gas Processors Association Standard:2337 Test for Hydrogen Sulfide and Carbon Dioxide inNatural Gas Using Length-of-Stain Tubes23. Terminology3.1 Definitions of Terms Specific to This Standard:3.1.1 detecto

7、r tube pumpa hand-operated pump of apiston or bellows type. It must be capable of drawing 100 mLper stroke of sample through the detector tube with a volumetolerance of 65 mL.3It must be specifically designed for usewith detector tubes.3.1.1.1 DiscussionA detector tube and pump togetherform a unit a

8、nd must be used as such. Each manufacturercalibrates detector tubes to match the flow characteristics oftheir specific pump. Crossing brands of pumps and tubes is notpermitted, as considerable loss of system accuracy is likely tooccur.33.1.2 gas sampling chamberany container that providesfor access

9、of the detector tube into a uniform flow of samplegas at atmospheric pressure and isolates the sample from thesurrounding atmosphere. A stainless steel needle valve (orpressure regulator) is placed between the source valve and thesampling chamber for the purpose of throttling the sampleflow. Flow ra

10、te should approximate 1 to 2 volume changes perminute or, at minimum, provide exit gas flow throughout thedetector tube-sampling period.3.1.2.1 DiscussionA suitable sampling chamber may bedevised from a polyethylene wash bottle of nominal 500-mL(16-oz) or 1-L (32-oz) size. The wash bottles internal

11、deliverytube provides for delivery of sample gas to the bottom of thebottle. A 14.7-mm (12-in.) hole cut in the bottles cap providesaccess for the detector tube and vent for the purge gas (see Fig.1). (An alternate flow-through sampler may be fashioned usinga 1-gal (3.8-L) “zipper”-type food storage

12、 bag. The flexibleline enters one corner of the bags open end and extends to thebottom of the bag. The opposite corner of the bags top issealed shut. The basic procedure for the sampler in Fig. 1applies.)3.1.2.2 DiscussionAn alternate sampling container is acollection bag made of a material suitable

13、 for the collection ofnatural gas (for example, polyester film). The sampling bagshould have a minimum capacity of 2 L.3.1.3 length-of-stain detector tubea sealed glass tube withbreak-off tips sized to fit the tube holder of the pump. Thereagent layer inside the tube, typically a silica gel substanc

14、ecoated with the active chemicals, must be specific for carbondioxide and produce a distinct color change when exposed to asample of gas containing carbon dioxide. Any substancesknown to interfere must be listed in the instructions accompa-nying the tubes. A calibration scale should be marked direct

15、lyon the tube; however, other markings that provide for easyinterpretation of carbon dioxide content from a separatecalibration scale supplied with the tubes shall be acceptable.1This test method is issued under the jurisdiction of ASTM Committee D03 onGaseous Fuels and is the direct responsibility

16、of Subcommittee D03.07 on Analysisof Chemical Composition of Gaseous Fuels.Current edition approved Nov. 1, 2011. Published March 2012. Originallyapproved in 1989. Last previous edition approved in 2006 as D498406. DOI:10.1520/D4984-06R11.2Available from Gas Processors Association, 6526 East 60th St

17、., Tulsa, OK74145.3 , First ed., American Industrial Hygiene Association, Akron, OH 44311.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.The calibration scale shall correlate carbon dioxide concentra-tion to the length of the color

18、stain. Shelf life of the detectortubes must be a minimum of two years from the date ofmanufacture when stored according to manufacturers recom-mendations.4. Summary of Test Method4.1 The sample is passed through a detector tube filled witha specially prepared chemical. Any carbon dioxide present int

19、he sample reacts with the chemical to produce a color changeor stain. The length of the stain produced in the detector tube,when exposed to a measured volume of sample, is directlyproportional to the amount of carbon dioxide present in thesample. A hand-operated piston or bellows-type pump is usedto

20、 draw a measured volume of sample through the tube at acontrolled rate of flow. The length of stain produced isconverted to parts per million (ppm) or percent (%) carbondioxide by comparison to a calibration scale supplied by themanufacturer for each box of detection tubes. The system isdirect readi

21、ng, easily portable, and completely suited to makingrapid spot checks for carbon dioxide under field conditions.(See Note 1.)5. Significance and Use5.1 The measurement of carbon dioxide in natural gas isimportant, because of the gas quality specifications, the corro-sive nature of carbon dioxide on

22、pipeline materials, and theaffects of carbon dioxide on utilization equipment.5.2 This test method provides inexpensive field screening ofcarbon dioxide. The system design is such that it may be usedby nontechnical personnel with a minimum of proper training.6. Interferences6.1 Detector tubes are us

23、ually subject to interferences fromgases and vapors other than the target substance. Such inter-ferences may vary among brands as a result of the use ofdifferent detection methods. Some detector tubes will have a“precleanse” layer designed to remove interferences up tosome maximum interferent level.

24、 Consult manufacturers in-structions for specific interference information.7. Procedure7.1 Select a sampling point that provides access to arepresentative sample of the gas being tested (source valve onthe main line). The sample point should be on top of thepipeline and equipped with a stainless ste

25、el sample probeextending into the middle third of the pipeline. Open the sourcevalve momentarily to clear the valve and connecting nipple offoreign materials.7.2 Install needle valve (or pressure regulator) at the sourcevalve outlet. Connect sampling chamber using the shortestlength of flexible tubi

26、ng possible (see Fig. 1). Most flexibletubing material will be suitable for carbon dioxide sampling;however, if the sampler is also used for other constituents suchas hydrogen sulfide, then choose tubing materials carefully.Avoid using tubing that reacts with or absorbs hydrogensulfide, such as copp

27、er or natural rubber. Use materials such asTFE-fluorocarbon, vinyl, polyethylene, or stainless steel.7.3 Open source valve. Open needle valve enough to obtainpositive flow of gas through chamber, in accordance with 3.1.2.Purge the container for at least 3 min (see Fig. 1).NOTE 2If a collection bag i

28、s used instead of a sampling chamber,follow 7.1 and 7.2, substituting the bag for the chamber. Follow 7.3,disconnecting the bag when filled. Deflate the bag to provide a purge, andfill a second time to provide a sample. The bag must be flattenedcompletely before each filling (see second Discussion i

29、n 3.1.2).7.4 Before each series of measurements, test the pump forleaks by operating it with an unbroken tube in place. Consultmanufacturers instructions for leak check procedure detailsand for maintenance instruction if leaks are detected. The leakcheck typically takes 1 min. A leaking pump used in

30、 fieldtesting will bias sample results low.7.5 Select the tube range that best encompasses carbondioxide concentration. Reading accuracy is improved when thestain length extends into the upper half of the calibration scale.Consult manufacturer guidelines for using multiple strokes toachieve a lower

31、range on a given tube.7.6 Break off the tube tips and insert the tube into the pump,observing the flow direction indication on the tube. Place thedetector tube into the sampling chamber through the accesshole, such that the tube inlet is near the chamber center (seeFig. 1).NOTE 3Detector tubes have

32、temperature limits of 0 to 40C (32 to104F), and sample gases must remain in that range throughout the test.Cooling probes are available for sample temperatures exceeding 40C.7.7 Operate the pump to draw the measured sample volumethrough the detector tube. Observe tube instructions whenapplying multi

33、ple strokes. Ensure that a positive flow ismaintained throughout the sample duration at the samplingchamber gas exit vent. Observe tube instructions for properFIG. 1 Apparatus SchematicD4984 06 (2011)2sampling time per pump stroke. The tube inlet must remain inposition inside the sampling chamber un

34、til sample is com-pleted. Many detector tube pumps have stroke finish indicatorsthat eliminate the need to time the sample.NOTE 4If a collection bag is used, draw the sample from the bag viaa flexible tubing connection. Do not squeeze the bag during sampling.Allow the bag to collapse under pump vacu

35、um, so that the pumps flowcharacteristics are not altered.NOTE 5It is very important to ensure that ambient air is not beingdrawn into the sample. Intrusion of ambient air into the sample will tendto bias the carbon dioxide readings low.7.8 Remove the tube from the pump and immediately readcarbon di

36、oxide concentration from the tubes calibration scaleor from the charts provided in the box of tubes. Read the tubeat the maximum point of the stain. If “channeling” hasoccurred (nonuniform stain length), read the maximum andminimum stain lengths and average the two. Consult tubeinstructions for any

37、special information in the event of multi-colored stains.NOTE 6If the calibration scale is not printed directly on the detectortube, be sure that any separate calibration chart is the proper match for thetube in use.7.9 If the number of strokes used differs from the number ofstrokes specified for th

38、e calibration scale, correct the reading asfollows:ppm corrected!5ppm reading!3specified strokesactual strokes7.10 Record the reading immediately, along with the gastemperature and the barometric pressure. Observe any tem-perature corrections supplied in the tube instructions. Altitudecorrections be

39、come significant at elevations above 2000 ft.Correct for barometric pressure as follows:ppm corrected!5 ppm reading!3760 mm Hgbarometric pressure in mm HgNOTE 7Even though the amount of chemicals contained in detectortubes is very small, the tubes should not be disposed of carelessly. Ageneral dispo

40、sal method includes soaking the opened tubes in water beforetube disposal. The water should be treated to a neutral pH before itsdisposal.8. Quality Assurance8.1 Detector tubes from each batch or lot of tubes should betested to conform the published accuracy, (generally 6 25 %).8.2 The tubes should

41、continue to meet the published accu-racy until the expiration date, if the tubes are shipped andstored per manufacturer instructions.9. Precision and Bias9.1 The accuracy of detector tube systems is generallyconsidered to be 625 %. This is based mainly on programsconducted by the National Institute

42、of Occupational Safety andHealth (NIOSH) in certifying detector tubes for low-levelcontaminants in air adapted to worker exposure monitoring.4NIOSH tested tubes at12 , 1, 2, and 5 times the threshold limitvalue (TLV) requiring 625 % accuracy at the three higherlevels and 35 % at the12 TLV level. (Fo

43、r example, CO2, witha TLV of 5000 ppm, was tested at levels 2500, 5000, 10 000,and 25 000 ppm.) The higher tolerance allowed at the low levelwas due to the loss of accuracy for shorter stain lengths.3NIOSH discontinued this program in 1983, and it was pickedup by the Safety Equipment Institute (SEI)

44、 in 1986.9.2 The Gas Processors Association reports an observederror of 68 % or better in tests of two brands of carbon dioxidedetector tubes (see 2.1, 2337).10. Keywords10.1 gaseous fuels; natural gasASTM International takes no position respecting the validity of any patent rights asserted in conne

45、ction with any item mentionedin this standard. Users of this standard are expressly advised that determination of the validity of any such patent rights, and the riskof infringement of such rights, are entirely their own responsibility.This standard is subject to revision at any time by the responsi

46、ble technical committee and must be reviewed every five years andif not revised, either reapproved or withdrawn. Your comments are invited either for revision of this standard or for additional standardsand should be addressed to ASTM International Headquarters. Your comments will receive careful co

47、nsideration at a meeting of theresponsible technical committee, which you may attend. If you feel that your comments have not received a fair hearing you shouldmake your views known to the ASTM Committee on Standards, at the address shown below.This standard is copyrighted by ASTM International, 100

48、 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959,United States. Individual reprints (single or multiple copies) of this standard may be obtained by contacting ASTM at the aboveaddress or at 610-832-9585 (phone), 610-832-9555 (fax), or serviceastm.org (e-mail); or through the ASTM website(www.astm.org). Permission rights to photocopy the standard may also be secured from the ASTM website (www.astm.org/COPYRIGHT/).4“NIOSH Certification Requirements for Gas Detector Tube Units,” NIOSH-TC-012, 1978.D4984 06 (2011)3