FEASIBILITY OF ANALYSIS AND SCREENING OF PLASTICS FOR HEAVY METALS WITH PORTBALE XRAY FLUORESCENCE ANALYZER WITH MINIATURE XRAY TUBE_第1页
FEASIBILITY OF ANALYSIS AND SCREENING OF PLASTICS FOR HEAVY METALS WITH PORTBALE XRAY FLUORESCENCE ANALYZER WITH MINIATURE XRAY TUBE_第2页
FEASIBILITY OF ANALYSIS AND SCREENING OF PLASTICS FOR HEAVY METALS WITH PORTBALE XRAY FLUORESCENCE ANALYZER WITH MINIATURE XRAY TUBE_第3页
FEASIBILITY OF ANALYSIS AND SCREENING OF PLASTICS FOR HEAVY METALS WITH PORTBALE XRAY FLUORESCENCE ANALYZER WITH MINIATURE XRAY TUBE_第4页
FEASIBILITY OF ANALYSIS AND SCREENING OF PLASTICS FOR HEAVY METALS WITH PORTBALE XRAY FLUORESCENCE ANALYZER WITH MINIATURE XRAY TUBE_第5页
已阅读5页,还剩4页未读 继续免费阅读

下载本文档

版权说明:本文档由用户提供并上传,收益归属内容提供方,若内容存在侵权,请进行举报或认领

文档简介

1、feasibility of analysis and screening of plastics for heavy metals withportbale x-ray fluorescence analyzer with miniature x-ray tubestanislaw piorekniton llc, 900 middlesex turnpike, billerica, ma 01821abstractmetals and metal compounds have been used for many years in the manufacture of plasticpro

2、ducts. the metallic compounds added to plastics although encapsulated in polymer matrix, areusually not chemically bound to polymer molecules and consequently can be gradually released into theenvironment over the service life of a plastic made object.similarly, when disposing of plastic waste, eith

3、er by incineration or by placing it in a landfill, toxicmetals released from plastics can enter the atmosphere or leach into soil. environmentally responsiblehandling of plastics requires monitoring of potentially toxic elements in plastics during their production,recycling and disposal operations.i

4、n this paper we report on the application of a small, lightweight (1.5 kg), battery operatedportable x-ray fluorescence analyzer for in-situ analysis and screening of plastic for toxic metals.introductionelements such as lead, cadmium, chromium, mercury, bromine, tin and antimony are, or havebeen, a

5、dded to polymers as pigments, fillers, uv stabilizers, and flame retardants. typically theseelements are added as compounds which often do not chemically bond with molecules of plastic, butrather create a suspension in the solid plastic polymer. therefore, in time they may potentially dislodgefrom t

6、he plastics matrix. the finer the particles of added compound, the easier it is for them to beremoved. a visible symptom of this process is a hazing on the surface of some plastics caused bymigration of bromine from the bulk of the material to its surface. pvc based plastics contain considerableamou

7、nts of chlorine which, when released, facilitates the leaching of metals into the environment. thiscan create serious health and environmental problems, as most of these elements have been identifiedas toxic to humans. specifically, because many toys and objects of common use are made of plastics,th

8、ey pose a particular danger to small children. the initiatives undertaken to correct this growingproblem target the maximum allowable concentrations of toxic metals in plastics, and ultimately aim tocompletely eliminate them from production.the first regulations to specifically target heavy metals i

9、n plastics were introduced in the midnineties by the european community. the european community packaging directive - ec-directive94/62/eec, 1 regulates the total amount of metals such as cd, cr, hg and pb in plastic packagingmaterials to less than 100 mg/kg. another eu directive, 91/338/ec 2, sets

10、the maximum allowableconcentration of cadmium in plastics used for consumer goods at 100 mg/kg. in the us, proposition65 introduced in california banned cadmium from use. a separate effort is directed at proper handlingof plastic waste. specifically, european council directive 2002/96/ec on waste el

11、ectrical and electronicequipment (weee) 3, mandates the removal of all plastic containing brominated flame retardants, allmercury containing components, batteries, etc. from such wastethe effective enforcement of such regulations requires that sensitive and reliable methods andinstruments be readily

12、 available for responsible parties. for example, given the amount of importedgoods crossing borders every day, the task of customs inspectors to effectively inspect the goods ispossible only with a small, portable, easy to operate analytical tool(s) that can quickly identify andquantify prohibited e

13、lements in plastic products.over the last decade, small, lightweight field-portable xrf analyzers (or fpxrf) have becomeindispensable tools for accurate and rapid in-situ analysis and identification of alloys in metals production,fabrication and recycling. a second major use of these instruments has

14、 been in soil screening andanalysis for heavy metals 4. the problems encountered when attempting xrf analysis of plastics arein many ways similar to those that had to be addressed in analysis of soil. therefore, the use of portablexrf analyzer to measure the concentration levels of metals in plastic

15、s seems to be a natural extension ofits already tested capabilities for soil analysis.the principle of xrf analysisx-ray fluorescence analysis is based on the phenomenon of the emission of x-rays by the atomsof a sample when excited by an external source of radiation. if a gamma- or sufficiently ene

16、rgetic x-rayfrom an isotope or x-ray tube impinges on an atom of the sample material, it may eject one of the innershell electrons of the atom. the vacancy created is almost instantaneously (in less than 10-8 sec.) filledby one of the electrons from the higher energy shell. the energy difference bet

17、ween the two energyshells involved in the process is emitted in the form of x-ray radiation. we call this radiation acharacteristic x-ray because its energy is specific and unique to each atom. by being able to measurethe energy and intensity of the characteristic x-rays, we realize qualitative and

18、quantitative aspects ofxrf analysis.x-ray fluorescence spectrometry has long been recognized as a major analytical tool, originally inthe wavelength dispersive (wdxrf), and later also in the energy dispersive (edxrf) version. thereprobably is no metallurgical facility without at least one wdxrf spec

19、trometer. the speed, reliability andtruly nondestructive character of the xrf method make it suitable not only for laboratory applications, butespecially for field and plant use. however, the successful expansion of x-ray fluorescence analysis fromlaboratory to plant and field environments was made

20、possible only by the recent availability of portablexrf analyzers. several critical factors have contributed to this, namely:-the availability of small, sealed radioisotope sources to excite the characteristic x-rays of thesample;-the availability of small, room temperature, high energy resolution d

21、etectors;-the availability of powerful microprocessors; and-the availability of compact, high capacity, rechargeable batteries to make the instrumentindependent of the ac power.in particular, developments in microprocessor technology have made it possible for portable,battery-operated x-ray analyzer

22、s to perform in real time complex analyzes of the x-ray spectra from thesample, followed by sophisticated data processing; a task previously assigned only to off-line computers.the portable, microprocessor based x-ray analyzers have been a real breakthrough by combining speedand truly nondestructive

23、 character of analysis (the instrument being brought to the sample and nototherwise) with an expert identification/sorting software. most recently, another technologicalbreakthrough - the development of a miniature, low power x-ray tube - improved the performance ofportable xrf analyzers and made th

24、em even easier to use. replacing the isotope with an x-ray tubenot only improves the instruments sensitivity and analytical range, but also makes it easier to transportand overall safer to operate because no x-rays are emitted from the x-ray tube once the power to theinstrument is turned off.experim

25、entalthe analyzerthe portable analyzer used in this work is shown in figure 1. it is an ergonomically designedhand-held, lightweight (1.5 kg), environmentally sealed, battery operated unit. it employs a miniature, lowpower x-ray tube as the source of sample excitation. the end-window, transmission a

26、node tube operates2at 38 kv of high voltage and 20 ua of current. a high resolutionsilicon p-i-n diode detector (energy resolution better than 230 ev )is used to detect and register characteristic x-rays from thesample. the instrument is powered by a rechargeable li-ionbattery which sustains its ope

27、ration for up to about 8 to 10 hours.a proprietary operating system controls all the functional blocks ofthe analyzer. the operator communicates with the analyzer via abuilt-in touch screen display with an intuitive user interface. thefront end (nose) of the analyzer is a flat plate with a small 10

28、by20 mm rectangular window sealed with polyimide foil. this plateprovides a repeatable means of sample presentation for analysis.the measurement of solid, extended samples is performed bypressing the nose of the instrument against the analyzed objectand pulling the trigger. alternatively, to measure

29、 bulk samplessuch as powders or pellets, the instrument may be put into aspecial stand which accepts sample cups filled with bulk materialas shown in figure 2.the primary result of the measurement is an x-rayspectrum of the sample. it is the information extracted from thespectrum that is then conver

30、ted into qualitative and quantitativedata of the elemental concentrations in the sample. examples figure 1. portable x-ray analyzer, niton model xlt-794of x-ray spectra from a sample of plastic measured with the analyzer described above are shown infigure 3. in this case, the sample has been a handl

31、e of a screwdriver. the two spectra shown,marked with black and yellow color, represent the black and yellow areas of the handle, respectively.the yellow spectrum reveals the presence of lead (two major peaks at 10.5 and 12.6 kev) in the yellowsections of the handle. the integral of any lead peak is

32、 a measure of the lead content.figure 2. portable x-ray analyzer measuring bulk samples in specialstand. also shown are sample preparation accessories.376543210ticrpbcraftsman screwdriver - yellowsectioncraftsman screwdriver - blacksectionsb23456789 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26

33、 27 28 29 30 31 32 33 34energy of x-rays, kevfigure 3. an example of an x-ray spectrum of plastic object, here the hdpe handle of a screwdriver. notethat lead, titanium and chromium are present in the yellow sections of the handle. it appears that yellowsections are painted with paint containing tit

34、ania and lead chromate pigment. antimony is present inplastics. a relatively thin layer of yellow paint does not absorb antimony x-rays. this example illustratesexcellent identification capabilities of the xrf method.analytical approachin order to test the capabilities of the analyzer, a number of p

35、olymer-based samples of knowncompositions were procured. these samples were prepared from pvc and pe resins by adding to themantimony, bromine, titanium, chromium, mercury, cadmium and lead. the concentrations of additiveswere varied to imitate the concentration ranges encountered in real polymers.

36、while concentrations ofheavy metals were maintained between 0 to 1000 mg/kg, the other elements were allowed to reachseveral percent levels. it is worth noting that there are very few polymer based certified materialsavailable, and those that do exist are prepared in polyethylene medium only 5, 6.th

37、e xrf analysis is known for the so called matrix effects which are manifestation of interactionof x-rays with the medium they pass through. in any analytical method, one expects the measuredsignal from a given element to be proportional, preferably linearly, to the elements concentration in thesampl

38、e. in xrf analysis this relation is generally nonlinear for two reasons. first, the element itselfabsorbs its own characteristic x-rays when its concentration in the sample increases. second, thepresence of another element in the sample also increases the absorption of x-rays from the analyte inques

39、tion. for example, two samples, each containing 5% iron in a polyethylene matrix will producedifferent intensities of iron if one of the samples will additionally contain, say, 10% titanium. should wenot be aware of this fact, we might infer a false conclusion about the iron concentration in samples

40、 fromthe iron intensities alone. in the past a number of methods (empirical, semi-empirical and mathematical)have been proposed to correct for these effects.based on earlier experience it has been determined that the best analytical approach to plasticsanalysis using xrf is the method of fundamental

41、 parameters (fp). this method utilizes the fact thatthe measured x-ray intensities of the elements in a sample can be fully described by a complete set ofmathematical equations. the equations tie together the physics of the interaction of x-rays with matter4 coun t rate, cp sand sample composition.

42、these equations can only be solved by iterative methods which requireconsiderable speed and computing power. the alternatives to the fp-based method are a classicalempirical calibration, or the so called compton normalization (cn) method. the empirical calibration hasthe advantage of being the most

43、accurate of all methods. however, its serious disadvantage is therequirement of availability of an extensive set of analyzed samples with compositions as close as possibleto those of unknown samples. given the number of various plastic materials, this requirement ispractically impossible to satisfy.

44、 the cn method, while being less demanding on the availability ofstandards, is not capable of handling wide concentration ranges encountered in the analysis of plastics.an excellent, in depth discussion of the calibration methods mentioned here can be found in reference 7.resultsaccuracy, precision

45、and minimum detection limitsall samples used in this study were measured for 200 sec each. samples prepared from pe orpvc resin were made into solid discs of 31 mm diameter, and at least 6 mm thick for pvc and 13 mmthick for pe. additional samples collected from various sources were all at least 4 m

46、m thick and coveredthe rectangular (10 by 20 mm) measuring window of the probe. some samples were available only as 3mm pellets. these were placed in 31 mm diameter by 20 mm high sample cups (chemplex industries).figure 4 shows measured data plotted against certified values for lead in pe and pvc sa

47、mples.as can be seen, the compton normalization (cn) method cannot handle high levels of bromine, whichoften is present at up to 20% concentrations in some plastics. similarly, higher concentrations ofantimony pose problems for the cn method as shown in figure 5 for cadmium. on the contrary, thefund

48、amental parameters method (fp) handles interferences quite well. note also, that the fp methodautomatically accounts for the type of plastic matrix, while the cn method is not reliable in this respect.pb in pvc and pe plastics20001500100050000cn methodfp methodthese samples contain: 5% and 10% bromi

49、ne200400600mg/kg (cert.)800y = 1.042xr2 = 0.986710001200figure 4. measured v/s certified concentration of lead in pvc and non-pvc matrices. these data includesamples of lead in a pure matrix and in matrices containing up to several percents of ti, br, and sb, as wellas up to 1000 mg/kg of cd and cr.

50、5 m g /k g (m e as .)30002500cn methodfp methodcd in pvc and pe plastics20001500100050000samples in ovals contain from2 to 10 % of br and/or sb200400600mg/kg cd (cert.)8001000y = 1.0655xr2 = 0.98641200figure 5. measured v/s certified concentration of cadmium in pvc and non-pvc matrices. these datain

51、clude samples of cadmium in a pure matrix and in matrices containing up to several percent of ti, br, andsb, as well as up to 1000 mg/kg of pb and cr.in summary, figures 4 and 5 show consistently more accurate analysis with fp than with cn. ofparticular note is the excellent ability of the algorithm

52、 to compensate for br and sb over a wide range ofconcentrations; the slopes and r2 factors are close to 1.0 in all cases.the instrument minimum detection limits (mdl) were determined from the series of replicatemeasurements of samples with low and high concentrations of interfering elements but low

53、(below 100mg/kg) or zero concentrations of the analytes. three standard deviations, as calculated from theappropriate series, is a measure of the mdl for a given analyte. these are reported in table 1. themdl and precision data for lead and cadmium appear satisfactory. that is not the case for chromium. inorder to improve the chromium performance of the analyzer it will be necessary to make minor hardwareimprovements in the front end of the instrument. in any case, the present precision and mdl can beimproved by extending the mea

温馨提示

  • 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。图纸软件为CAD,CAXA,PROE,UG,SolidWorks等.压缩文件请下载最新的WinRAR软件解压。
  • 2. 本站的文档不包含任何第三方提供的附件图纸等,如果需要附件,请联系上传者。文件的所有权益归上传用户所有。
  • 3. 本站RAR压缩包中若带图纸,网页内容里面会有图纸预览,若没有图纸预览就没有图纸。
  • 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. 人人文库网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,对用户上传分享的文档内容本身不做任何修改或编辑,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。

评论

0/150

提交评论