ASTM D3608-1995(2005) Standard Test Method for Nitrogen Oxides (Combined) Content in the Atmosphere by the Griess-Saltzman Reaction《用griss-saltzman反应法测定大气中氧化氮(结合)含量的标准试验方法》.pdf

《ASTM D3608-1995(2005) Standard Test Method for Nitrogen Oxides (Combined) Content in the Atmosphere by the Griess-Saltzman Reaction《用griss-saltzman反应法测定大气中氧化氮(结合)含量的标准试验方法》.pdf》由会员分享，可在线阅读，更多相关《ASTM D3608-1995(2005) Standard Test Method for Nitrogen Oxides (Combined) Content in the Atmosphere by the Griess-Saltzman Reaction《用griss-saltzman反应法测定大气中氧化氮(结合)含量的标准试验方法》.pdf（5页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: D 3608 95 (Reapproved 2005)Standard Test Method forNitrogen Oxides (Combined) Content in the Atmosphere bythe Griess-Saltzman Reaction1This standard is issued under the fixed designation D 3608; the number immediately following the designation indicates the year oforiginal adoption or,

2、in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon (e) indicates an editorial change since the last revision or reapproval.1. Scope1.1 This test method covers the manual determination of thecombined nitrogen dioxide

3、 (NO2) and nitric oxide (NO)content, total NOx; in the atmosphere in the range from 4 to10 000 g/m3(0.002 to 5 ppm (v).1.2 The maximum sampling period is 60 min at a flow rateof 0.4 L/min.1.3 The values stated in SI units are to be regarded asstandard. The values given in brackets are for informatio

4、n only.1.4 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 determine the applica-bility of regulatory limitations prior to use.2. Refer

5、enced Documents2.1 ASTM Standards:2D 1071 Test Methods for Volumetric Measurement of Gas-eous Fuel SamplesD 1193 Specification for Reagent WaterD 1356 Terminology Relating to Sampling and Analysis ofAtmospheresD 1357 Practice for Planning the Sampling of the AmbientAtmosphereD 3195 Practice for Rota

6、meter CalibrationD 3609 Practice for Calibration Techniques Using Perme-ation TubesD 3631 Test Methods for Measuring Surface AtmosphericPressureE1 Specification for ASTM Liquid-in-Glass ThermometersE 128 Test Method for Maximum Pore Diameter and Per-meability of Rigid Porous Filters for Laboratory U

7、se3. Terminology3.1 DefinitionsFor definitions of terms used in this testmethod, refer to Terminology D 1356.4. Summary of Test Method4.1 The NO is quantitatively (1)3converted to NO2by achromic acid oxidizer. The resulting NO2, plus the NO2alreadypresent, are absorbed in an azo-dye-forming reagent

8、(2). Ared-violet color is produced within 15 min, the intensity ofwhich is measured spectrophotometrically at 550 nm.5. Significance and Use5.1 Both NO2and NO play an important role inphotochemical-smog-forming reactions. In sufficient concen-trations NO2is deleterious to health, agriculture, materi

9、als, andvisibility.5.2 In combustion processes, significant amounts of NOmay be produced by combination of atmospheric nitrogen andoxygen; at ambient temperatures, NO can be converted to NO2by oxygen and other atmospheric oxidants. Nitrogen dioxidealso may be generated from processes involving nitri

10、c acid,nitrates, the use of explosives, and welding.6. Interferences6.1 Any significant interferences due to sulfur dioxide (SO2)should be negated by the oxidation step. The addition ofacetone to the reagent retards color-fading by forming atemporary addition product with SO2. This will protect ther

11、eagent from incidental exposure to SO2and will permitreading the color intensity within 4 to 5 h (instead of the 45 minrequired without acetone) without appreciable losses.6.2 A five-fold ratio of ozone to NO2will cause a smallinterference, the maximal effect occurring in 3 h. The reagentassumes a s

12、lightly orange tint.1This test method is under the jurisdiction of ASTM Committee D22 on AirQuality and is the direct responsibility of Subcommittee D22.03 on AmbientAtmospheres and Source Emissions.Current edition approved Oct. 1, 2005. Published January 2006. Originallyapproved in 1977. Last previ

13、ous edition approved in 2000 as D 3608 - 95 (2000)e1.2For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.3The bol

14、dface numbers in parentheses refer to the list of references appended tothis test method.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.6.3 The interferences from nitrous oxide and nitrogen pen-toxide, and other gases that might be

15、found in polluted air areconsidered to be negligible.7. Apparatus7.1 Sampling ProbeA glass or TFE-fluorocarbon (pre-ferred) tube, 6 to 10 mm in diameter, provided with adownward-facing intake (funnel or tip). The dead volume ofthe system should be kept minimal, to avoid loss of NOxon thesurfaces of

16、the apparatus.7.2 Oxidizer TubeSoak 14 to 16-mesh firebrick or116-in.1.5 mm molecular sieve pellets in a 17 % aqueous solution ofchromium trioxide (CrO3) for 10 to 30 min. After draining theexcess solution and drying in an oven at 105C for 30 min, thesolid oxidizer has a dull pink color. This color

17、changes to richyellow (active color) after 24-h equilibration with ambient airat 40 to 70 % relative humidity, or after drawing ambient airthrough at a flow rate of 0.5 L/min for 1 h. A change in colorto a greenish brown indicates the exhaustion of oxidizingability, and progresses with a sharp bound

18、ary. Place about 3 gof the oxidizer in a 30-mL midget impinger, or fill a 5-mm tubeto a height of 80 mm and plug each end with glass wool.7.3 AbsorberAn all-glass bubbler with a 60-m maxi-mum pore diameter frit, commonly labeled “coarse,” similar tothat illustrated in Fig. 1.7.3.1 The porosity of th

19、e fritted bubbler, as well as thesampling flow rate, affect absorption efficiency. An efficiencyof over 95 % may be expected with a flow rate of 0.4 L/min orless and a maximum pore diameter of 60 m. Frits having amaximum pore diameter less than 60 m will have a higherefficiency, but will require an

20、inconvenient pressure drop forsampling.7.3.2 Measure the porosity of an absorber in accordancewith Test Method E 128. If the frit is clogged or visiblydiscolored, carefully clean with concentrated chromic-sulfuricacid mixture, rinse well with water, and redetermine themaximum pore diameter.7.3.3 Rin

21、se the bubbler thoroughly with water and allow todry before using.7.4 Mist Eliminator or Gas Drying Tube filled with acti-vated charcoal or soda lime is used to prevent damage to theflowmeter and pump.7.5 Air-Metering DeviceA calibrated glass variable-areaflowmeter, or dry gas meter coupled with a f

22、low indicatorcapable of accurately measuring a flow of 0.4 L/min is suitable.7.6 ThermometerASTM Thermometer 33C, meeting therequirements of Specification E1, will be suitable for mostapplications of the method.7.7 Manometer, accurate to 670 Pa 0.20 in. Hg.7.8 Air PumpA suction pump capable of drawi

23、ng therequired sample flow for intervals of up to 60 min.7.9 Spectrophotometer or ColorimeterA laboratory in-strument suitable for measuring the intensity of the red-violetcolor at 550 nm, with stoppered tubes or cuvettes. Thewavelength band-width is not critical for this determination.7.10 Stopwatc

24、h or Timer.8. Reagents and Materials8.1 Purity of ReagentsReagent grade chemicals shall beused in all tests.All reagents shall conform to the specificationsof the Committee on Analytical Reagents of the AmericanChemical Society, where such specifications are available.4Other grades may be used, prov

25、ided it is first ascertained thatthe reagent is of sufficiently high purity to permit its usewithout lessening the accuracy of the determination.8.2 Purity of WaterWater shall be deionized water inaccordance with Specification D 1193 for Type I and II reagentwater. Water must be nitrite-free.8.3 Abs

26、orbing ReagentDissolve5gofanhydrous sulfa-nilic acid (or 5.5 g of the monohydrate) in almost a litre ofwater containing 140 mL of glacial acetic acid. Gentle heatingis permissible to speed up the process. To the cooled mixture,add 20 mL of the 0.1 % stock solution of N-(1-naphthyl)-ethylenediamine d

27、ihydrochloride and 10-mL acetone. Dilute to1 L. The solution will be stable for several months if keptwell-stoppered in a brown bottle in the refrigerator. Theabsorbing reagent must be at room temperature before use.Avoid lengthy contact with air during both preparation and use,since absorption of n

28、itrogen dioxide will discolor the reagent.8.4 Chromic Acid OxidantDissolve 17 g of chromiumtrioxide (CrO3) in 100 mL of water.8.5 N-(1-Naphthyl)-Ethylenediamine Dihydrochloride,Stock Solution (0.1 %)Dissolve 0.1 g of the reagent in 100mL of water. The solution will be stable for several months ifkep

29、t well-stoppered in a brown bottle in the refrigerator.(Alternatively, weighed small amounts of the solid reagent maybe stored.)4Reagent Chemicals, American Chemical Society Specifications, AmericanChemical Society, Washington, DC. For suggestions on the testing of reagents notlisted by the American

30、 Chemical Society, see Analar Standards for LaboratoryChemicals, BDH Ltd., Poole, Dorset, U.K., and the United States Pharmacopeiaand National Formulary, U.S. Pharmacopeial Convention, Inc. (USPC), Rockville,MD.FIG. 1 Fritted Bubbler for Sampling Combined Nitrogen OxidesD 3608 95 (2005)28.6 Sodium N

31、itrite (NaNO2), Standard Solution (0.0246g/L)One mL of this working solution of NaNO2produces acolor equivalent to that of 20 g of NO2in 1 L of air at 101 kPa29.92 in. Hg and 25C (see 10.2.2). Prepare fresh just beforeuse by diluting from a stock solution containing 2.460 g/L ofNaNO2(calculated as 1

32、00 %). It is desirable to assay the solidreagent (3). The stock solution is stable for 90 days at roomtemperatures, and for a year in a brown bottle under refrigera-tion.8.7 NO2Permeation DeviceSee Practice D 3609.9. Sampling9.1 Sampling procedures are described in Section 11. Dif-ferent combination

33、s of sampling rates and time may be chosento meet special needs, but sample volumes and air flow ratesmust be adjusted so that linearity is maintained betweenabsorbance and concentration over the dynamic range.9.2 See Practices D 1357 for sampling guidelines.10. Calibration and Standardization10.1 S

34、ampling EquipmentIf a flowmeter is used to mea-sure sample air, calibrate it prior to use using Practice D 3195.If a gas meter is used, calibrate it prior to use in accordancewith Test Method D 1071.10.2 Analysis:10.2.1 Recommended Procedure:10.2.1.1 Calibrated permeation tubes that contain liquefie

35、dNO2can be used to prepare standard concentrations of NO2inair (4). See Practice D 3609 for details. Analyses of theseknown concentrations give calibration curves that simulate allthe operational conditions performed during the sampling andchemical procedures. This calibration curve includes the im-

36、portant correction for collection efficiency at various concen-trations of NO2.10.2.1.2 Prepare or obtain a TFE-fluorocarbon permeationtube that emits NO2at a rate of 0.1 to 0.2 g/min (0.05 to 0.1L/min at standard conditions of 25C and 101.3 kPa 29.92 in.Hg. Calibrate permeation tubes under a stream

37、 of dry nitrogen,using Practice D 3609.10.2.1.3 To prepare standard concentrations of NO2as-semble the apparatus, as shown in Practice D 3609, consistingof a water-cooled condenser; constant-temperature water bathmaintained at 20C; cylinders containing pure dry nitrogen andpure dry air, with appropr

38、iate pressure regulators; needlevalves and flowmeters for the nitrogen and dry air diluent gasstreams. Bring the diluent gases to temperature by passagethrough a 2-m long copper coil immersed in the water bath.Insert a calibrated permeation tube into the central tube of thecondenser maintained at 20

39、C by circulating water from theconstant-temperature bath and pass a stream of nitrogen overthe tube at a fixed rate of approximately 50 mL/min. Dilute thisgas stream to the desired concentration by varying the flow rateof the “clean dry air.” This flow rate can normally be variedfrom 0.2 to 15 L/min

40、. The flow rate of the sampling systemdetermines the lower limit for the flow rate of diluent gases.The flow rates of the nitrogen and the diluent air must bemeasured to an accuracy of 1 to 2 %. With a tube permeatingNO2at a rate of 0.1 L/min (0.19 g/min), the range ofconcentration of NO2will be bet

41、ween 20 to 1000 g/m3(0.01to 0.50 ppm (v), a generally satisfactory range for ambient airconditions. When higher concentrations are desired, calibrateusing longer permeation tubes.10.2.1.4 Procedure for Preparing Simulated CalibrationCurvesA multitude of curves may be prepared by selectingdifferent c

42、ombinations of sampling rate and sampling time. Thefollowing description represents a typical procedure for ambi-ent air sampling of short duration. The system is designed toprovide an accurate measure of NO2in the 40 to 10 000 g/m3(0.02 to 5 ppm (v) range. It can be modified to meet specialneeds.10

43、.2.1.5 The dynamic range of the colorimetric procedurefixes the total volume of the sample at 24 L, then to obtainlinearity between the absorbance of the solution and theconcentration of NO2in parts per million by volume, select aconstant sampling time. This fixing of sampling time is alsodesirable

44、from a practical standpoint. In this case, select asampling time of 60 min. Then, to obtain a 24-L samplerequires a flow rate of 0.4 L/min. Calculate the concentration ofstandard NO2in air as follows:C 5P1000!R 1 r(1)where:C = concentration of NO2g/m3,P = permeation rate, g/min,R = flow rate of dilu

45、ent air, L/min,r = flow rate of diluent nitrogen, L/min, and1000 = conversion factor to convert L to m3.10.2.1.6 A plot of the concentration of NO2in g/m3(x-axis) against absorbance of the final solution (y-axis) willyield a straight line, the inverse or the slope of which is thefactor for conversio

46、n of absorbance to g/m3. This factorincludes the correction for collection efficiency. Any deviationfrom linearity at the lower concentration range indicates achange in collection efficiency of the sampling system. Actu-ally, the standard concentration of 20 g/m3is slightly belowthe dynamic range of

47、 the method. If this is the range of interest,the total volume of air collected should be increased to obtainsufficient color within the dynamic range of the colorimetricprocedure. Also, once the calibration factor has been estab-lished under simulated conditions, the conditions can bemodified so th

48、at the concentration of NO2is a simple multipleof the absorbance of the colored solution.10.2.2 Alternate Procedure:10.2.2.1 Standardization is based upon the empirical obser-vation (5) that 0.82 mol of NaNO2produces the same color as1 mol of NO2. One mL of the working standard contains 24.6g of NaN

49、O2. Since the molecular weight of NaNO2is 69.1,this is equivalent to: (24.6/69.1) 3 (46.0/0.82) = 20 g of NO2.10.2.2.2 For convenience, standard conditions are taken as101 kPa 29.92 in. Hg and 25C, at which the molar gasvolume is 24.47 L. This is very close to the standard conditionsused for air-handling equipment, 101 kPa 29.92 in. Hg,21.1C 70F, and 50 % relative humidity, at which the molargas volume is 24.76 L, or 1.2 % greater. Ordinarily, thecorrection of the sample volume to these standard conditions isslight and may b