ImageVerifierCode 换一换
格式:PDF , 页数:11 ,大小:182.67KB ,
资源ID:528366      下载积分:5000 积分
快捷下载
登录下载
邮箱/手机:
温馨提示:
如需开发票,请勿充值!快捷下载时,用户名和密码都是您填写的邮箱或者手机号,方便查询和重复下载(系统自动生成)。
如填写123,账号就是123,密码也是123。
特别说明:
请自助下载,系统不会自动发送文件的哦; 如果您已付费,想二次下载,请登录后访问:我的下载记录
支付方式: 支付宝扫码支付 微信扫码支付   
注意:如需开发票,请勿充值!
验证码:   换一换

加入VIP,免费下载
 

温馨提示:由于个人手机设置不同,如果发现不能下载,请复制以下地址【http://www.mydoc123.com/d-528366.html】到电脑端继续下载(重复下载不扣费)。

已注册用户请登录:
账号:
密码:
验证码:   换一换
  忘记密码?
三方登录: 微信登录  

下载须知

1: 本站所有资源如无特殊说明,都需要本地电脑安装OFFICE2007和PDF阅读器。
2: 试题试卷类文档,如果标题没有明确说明有答案则都视为没有答案,请知晓。
3: 文件的所有权益归上传用户所有。
4. 未经权益所有人同意不得将文件中的内容挪作商业或盈利用途。
5. 本站仅提供交流平台,并不能对任何下载内容负责。
6. 下载文件中如有侵权或不适当内容,请与我们联系,我们立即纠正。
7. 本站不保证下载资源的准确性、安全性和完整性, 同时也不承担用户因使用这些下载资源对自己和他人造成任何形式的伤害或损失。

版权提示 | 免责声明

本文(ASTM E1303-1995(2010) 7500 Practice for Refractive Index Detectors Used in Liquid Chromatography《液相色谱法用折射指数检测器的操作规程》.pdf)为本站会员(sofeeling205)主动上传,麦多课文库仅提供信息存储空间,仅对用户上传内容的表现方式做保护处理,对上载内容本身不做任何修改或编辑。 若此文所含内容侵犯了您的版权或隐私,请立即通知麦多课文库(发送邮件至master@mydoc123.com或直接QQ联系客服),我们立即给予删除!

ASTM E1303-1995(2010) 7500 Practice for Refractive Index Detectors Used in Liquid Chromatography《液相色谱法用折射指数检测器的操作规程》.pdf

1、Designation: E1303 95 (Reapproved 2010)Standard Practice forRefractive Index Detectors Used in Liquid Chromatography1This standard is issued under the fixed designation E1303; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the yea

2、r 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 practice covers tests used to evaluate the perfor-mance and to list certain descriptive specifications of ar

3、efractive index (RI) detector used as the detection componentof a liquid chromatographic (LC) system.1.2 This practice is intended to describe the performance ofthe detector both independent of the chromatographic system(static conditions, without flowing solvent) and with flowingsolvent (dynamic co

4、nditions).1.3 The values stated in SI units are to be regarded as thestandard.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 deter

5、mine the applica-bility of regulatory limitations prior to use.2. Referenced Documents2.1 ASTM Standards:2E386 Practice for Data Presentation Relating to High-Resolution Nuclear Magnetic Resonance (NMR) Spectros-copy3. Significance and Use3.1 Although it is possible to observe and measure each ofsev

6、eral characteristics of a detector under different and uniqueconditions, it is the intent of this practice that a complete set ofdetector test results should be obtained under the same oper-ating conditions. It should also be noted that to specifycompletely a detectors capability, its performance sh

7、ould bemeasured at several sets of conditions within the useful rangeof the detector.3.2 The objective of this practice is to test the detector underspecified conditions and in a configuration without an LCcolumn. This is a separation independent test. In certaincircumstances it might also be necess

8、ary to test the detector inthe separation mode with an LC column in the system, and theappropriate concerns are also mentioned. The terms and testsdescribed in this practice are sufficiently general so that theymay be adapted for use at whatever conditions may be chosenfor other reasons.4. Noise, Dr

9、ift, and Flow Sensitivity4.1 Descriptions of Terms Specific to This Standard:4.1.1 short term noisethis noise is the mean amplitude inrefractive index units (RIU) for random variations of thedetector signal having a frequency of one or more cycles perminute. Short term noise limits the smallest sign

10、al detectableby an RI detector, limits the precision attainable, and sets thelower limit on the dynamic range. This noise corresponds toobserved noise of the RI detector only. (The actual noise of theLC system may be larger or smaller than the observed value,depending upon the method of data collect

11、ion, or signalmonitoring of the detector, since observed noise is a function ofthe frequency, speed of response and the band width of therecorder or other electronic circuit measuring the detectorsignal.)4.1.2 long term noisethis noise is the maximum ampli-tude in RIU for random variations of the de

12、tector signal withfrequencies between 6 and 60 cycles per h (0.1 and 1.0 cyclesper min). It represents noise that may be mistaken for alate-eluting peak. This noise corresponds to the observed noiseonly and may not always be present.4.1.3 driftthe average slope of the long term noise enve-lope expre

13、ssed in RIU per hour as measured over a period of1h.4.1.4 staticrefers to the noise and drift measured underconditions of no flow.4.1.5 dynamicrefers to the noise and drift measured at aflow rate of 1.0 mL/min.4.1.6 flow sensitivitythe rate of change of signal displace-ment (in RIU) vs flow rate (in

14、 mL/min) resulting from stepchanges in flow rate calculated at 1 mL/min as described in4.3.12.4.2 Test Conditions:4.2.1 The same test solvent must be used in both sample andreference cells. The test solvent used and its purity should bespecified. Water equilibrated with the laboratory atmosphere1Thi

15、s practice is under the jurisdiction of ASTM Committee E13 on MolecularSpectroscopy and Separation Science and is the direct responsibility of Subcom-mittee E13.19 on Separation Science.Current edition approved Nov. 1, 2010. Published November 2010. Originallyapproved in 1989. Last previous edition

16、approved in 2005 as E1303 95 (2005).DOI: 10.1520/E1303-95R10.2For 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.

17、1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.containing minimum impurities is the preferred test solvent formeasuring noise and drift. Water for this purpose (preferablypurified by distillation, deionization, or reverse osmosis)sh

18、ould be drawn, filtered through a 0.45-m filter, and allowedto stand in a loosely covered container for several hours atambient temperature in the laboratory in which testing is to becarried out. This will ensure complete equilibration of thewater with the gases in the laboratory atmosphere.NOTE 1It

19、 is essentially impossible to maintain a constant RI value ofde-gassed water and of very dilute samples in de-gassed water. This is dueto the fact that the difference in refractive index between completelyde-gassed water and atmosphere-equilibrated water is 1.5 3 106RIU.3Thus, small differences in t

20、he concentration of dissolved gases betweenthe sample and the trapped reference can lead to significant errors inmeasurement of solutions where the expected difference in RI due tosolute is of the order of 106RIU or less. Therefore, in order to minimizeerror in determining samples with small RIU dif

21、ferences between them,atmosphere-equilibrated water (5.2.1) is recommended as the solvent fordetermining linearity and minimum detectability (Section 5).4.2.2 The detector should be located at the test site andswitched on at least 24 h prior to the start of testing. Somedetectors provide an oven to

22、thermostat the optics assembly.The oven should be set at a suitable temperature, following themanufacturers recommendations, and this temperature shouldbe noted and maintained throughout the test procedures.4.2.3 Linearity and speed of response of the recorder orother data acquisition device used sh

23、ould be such that it doesnot distort or otherwise interfere with the performance of thedetector.4If additional amplifiers are used between the detectorand the final readout device, their characteristics should alsofirst be established.4.3 Methods of Measurement:4.3.1 Connecta1m(39.37 in.) length of

24、clean, dry,stainless steel tubing of 0.25 mm (0.009 to 0.01 in.) insidediameter in place of the analytical column. The tubing can bestraight or coiled to minimize the space requirement. Thetubing should terminate in standard low dead volume fittings toconnect with the detector and to the pump. Comme

25、rcialchromatographs may already contain some capillary tubing toconnect the pump to the injection device. If this is of a similardiameter to that specified, it should be included in the 1.0 mlength; if significantly wider, it should be replaced for this test.4.3.2 Repeatedly rinse the reservoir and

26、chromatographicsystem, including the detector, with the test solvent prepared asdescribed in 4.2.1, until all previous solvent is removed fromthe system. Fill the reservoir with the test solvent.4.3.3 Thoroughly flush the reference cell with the samesolvent; keep the reference cell static.4.3.3.1 It

27、 may be necessary to flush both sample andreference cells with an intermediate solvent (such as methanolor acetone), if the solvent previously used in the system isimmiscible with the test solvent.4.3.4 Allow the chromatographic system to stabilize for atleast 60 min without flow. The detector range

28、, Note 2, shouldbe set such that the amplitude of short term noise may be easilymeasured. Ideally, the output should contain no filtering of thesignal. If the filtering cannot be turned off, the minimum timeconstant should be set and noted in the evaluation. Manuals ormanufacturers should be consult

29、ed to determine if time con-stant and detector range controls are coupled, and informationshould be obtained to determine if they can be decoupled fortesting. Set the recorder zero to near mid-scale. Record at least1 h of baseline under these static conditions, during which timethe ambient temperatu

30、re should not change by more than 2C.NOTE 2RI detectors will have one or more controls labeled attenua-tion, range, sensitivity, and scale factor. All are used to set the full scalerange (in RIU) of an output display device such as a strip chart recorder.4.3.5 Draw pairs of parallel lines, each betw

31、een12 to 1 minin length, to form an envelope of all observed randomvariations over any 15-min period (Fig. 1). Draw the parallellines in such a way as to minimize the distance between them.Measure the distance perpendicular to the time axis betweenthe parallel lines. Convert this value to RIU (5.2.9

32、). Calculatethe mean value over all the segments; this value is the staticshort term noise.4.3.6 Now mark the center (center of gravity) of eachsegment over the 15-min period of the short term noise3Munk, M. N., Liquid Chromatography Detectors, (T. M. Vickrey, Ed.), MarcelDekker, New York and Basel,

33、 1983, pp. 165204.4Bonsall, R. B., “The Chromatography SlaveThe Recorder,” Journal of GasChromatography, Vol 2, 1964, pp. 277284.FIG. 1 Examples for the Measurement of Short Term Noise, LongTerm Noise and DriftE1303 95 (2010)2measurement. Draw a series of parallel lines to these centers,each 10 min

34、in length (Fig. 1), and choose that pair of lineswhose distance apart perpendicular to the time axis is greatest.This distance is the static long term noise.4.3.7 Draw the pair of parallel lines, over the1hofmeasurement, that minimizes the distance perpendicular to thetime axis between the parallel

35、lines. The slope of either line,measured in RIU/h, is the static drift.4.3.8 Set the solvent delivery system to a flow rate that haspreviously been shown to deliver 1.0 mL/min under the sameconditions of capillary tubing, solvent, and temperature. Allowat least 15 min to stabilize. Set the recorder

36、zero nearmid-scale. Record at least1hofbaseline under these flowingconditions, during which time the ambient temperature shouldnot change by more than 2C.4.3.9 Draw pairs of parallel lines, measure the perpendiculardistances, and calculate the dynamic short term noise, in themanner described in 4.3.

37、5 for the static short term noise.4.3.10 Make the measurement for the dynamic long termnoise following the procedure outlined in 4.3.6.4.3.11 Draw the pair of parallel lines in accordance with4.3.7. The slope of this line is the dynamic drift.4.3.12 Stop the chromatographic flow.Allow at least 15 mi

38、nfor re-equilibration. Set the recorder at about 5 % of full scaleand leave the detector range setting at the value used for thenoise measurements. Set the solvent delivery system at a flowrate of 0.5 mL/min. Run for 15 min, or more if necessary forre-equilibration, at a slow recorder speed. Increas

39、e the flow rateto 1.0 mL/min and record for 15 min or more. Run at 2.0, 4.0,and 8.0 mL/min if the pressure flow limit of the chromato-graphic system is not exceeded. If necessary, adjust the detectorrange to maintain an on-scale response.4.3.13 Draw a horizontal line through the plateau producedat e

40、ach flow rate, after a steady state is reached (Fig. 2).Measure the vertical displacement between these lines, andexpress in RIU (5.2.9). Plot these values versus flow rate. Drawa smooth curve connecting the points and draw a tangent at 1mL/min (Fig. 3). Express the slope of the line as the flowsens

41、itivity in RIU min/mL. It is preferred to give the numericalvalue and show the plot as well.5. Minimum Detectability, Linear Range, DynamicRange, and Calibration5.1 Descriptions of Terms Specific to this Standard:5.1.1 minimum detectabilitythat concentration of a spe-cific solute in a specific solve

42、nt that gives a signal equal totwice the static short-term noise.5.1.1.1 DiscussionThe static short-term noise is a mea-surement of peak-to-peak noise. A statistical approach to noisesuggests that a value of three times the rms (root-mean-square)noise would ensure that any value outside this range w

43、ould notbe noise with a confidence level of greater than 99 %. Sincepeak-to-peak noise is approximately five times the rmsnoise,4,5the minimum detectability defined in this practice is amore conservative estimate. Minimum detectability, as definedin this practice, should not be confused with the lim

44、it ofdetection in an analytical method using a refractive indexdetector.5.1.2 sensitivity (response factor)the signal output perunit concentration of the test substance in the test solvent, inaccordance with the following relationship:S 5 R/C (1)where:S = sensitivity (response factor), RIUL/g,R = me

45、asured detector response, RIU, andC = concentration of the test substance in the test solventg/L.5.1.3 linear rangethe range of concentrations of the testsubstance in the test solvent, over which the sensitivity of thedetector is constant to with 5 % as determined from the5Blair, E. J., Introduction

46、 to Chemical Instrumentation , McGraw-Hill, NewYork, NY, 1962, and Practice E386.FIG. 2 Example for the Measurement of Flow SensitivityFIG. 3 Example of Plot for Calculation of Flow SensitivityE1303 95 (2010)3linearity plot specified in 5.2.13. The linear range may beexpressed in three different way

47、s:5.1.3.1 As the ratio of the upper limit of linearity obtainedfrom the linearity plot, and the minimum linear concentration,both measured for the same test substance in the same testsolvent as follows:L.R. 5 Cmax/Cmin(2)where:L.R. = linear range of the detector,Cmax= upper limit of linearity obtain

48、ed from the linearityplot, g/L, andCmin= minimum linear concentration, g/L, as defined in5.2.13.1, the minimum linear concentration shouldalso be stated.5.1.3.2 By giving the minimum linear concentration and theupper limit of linearity (for example, from 8.72 3 103g/L to8.72 3 101g/L).5.1.3.3 By giv

49、ing the linearity plot itself, with the minimumlinear concentration and the upper limit of linearity indicatedon the plot.5.1.4 Dynamic RangeThat range of concentrations of thetest substance in the test solvent, over which an incrementalchange in concentration produces an incremental change indetector signal. The upper limit is the highest concentration atwhich a slight further increase in concentration will give anobservable increase in detector signal. The dynamic range isthe ratio of these upper and lower limits. The dynamic range islarger than or equ

copyright@ 2008-2019 麦多课文库(www.mydoc123.com)网站版权所有
备案/许可证编号:苏ICP备17064731号-1