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PARAMETRIC AND SURFACTANT CHANGE EFFECTS

IN THE FUME ATOMIC SPECTRCKETRIC DETERMINATION OF COPPER

BY

JOSEPH E. IVANECKY III

THESIS FOR THE

DEGREE OF BACHELOR OF SCIENCE IN

CHEMISTRY

College of Liberal Arts and Soianoaa Univaraity of Illinoia

Urbana, Illinois

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UNIVERSITY OF ILLINOIS

JULY 26

THIS IS TO CERTIFY THAT THE THESIS PREPARED UNDER MY SUPERVISION BY ... JOSEPH E. IVANECKY III...

ENTITLE... IN THE FLAi'iE ATOMIC SPECTuQMKTnlC DETERMINATION OF COPPEK

IS APPROVED BY ME AS FULFILLING THIS PART OF THE REQUIREMENTS FOR THE DEGREE of..

HEAD OF DEPARTMENT OF.G.H&.-lI&T.f.Of.

It

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Parametrio and Surfactant Charge Kffeets

in the Flame Atoaio Speotrematrie Determination of Copper Abstract

Tht parametric dependenoe of aeroaol ionio redistribution

(AIR) for the determination of eopper in laminar flame atomic epeo- troeeopy is investigated. Speoifioally. effeots of flame oompo- sition. sample uptake rate, and impact bead position are considered Little dependenoe is noted, reflecting the high atomisation effi­ ciency of the analyte under the varied conditions. Surfaotant charge effeots. as predicted by the AIK model, were confirmed for both absorption and emission, and oharaeterised with respeot to surfaotant oonoentration. In addition to previously reported en­ hancements with the addition of anionio surfaotants. a desensiti- . sation was observed with oationie surfaotants. The effeots of

either ionic surfaotants were seen to be muoh larger than surfaoe tension effects as studied using a nonionio surfactant. In omis­ sion studies using a total consumption burner no effeots of AXh were noted, although an enhancement was observed at high concentra­

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ACKNOWLEDGEMENTS

Funding of this research, by donors of ths Petroleum Re­ search Fund, sdministsrsd by ths American Chemical Society, and a University of Illinois Biomedical Research Support Grant (fun­ ded by N. 1. i.) is gratefully acknowledged. Thanks are exten­ ded to Dr. Raymond S. Vogel for sharing essential instrumenta­ tion and personal insights. Dr. Kelsey D. Cook is acknowledged for extending this opportunity and sharing his talented ressaroh group. Special thanks and appreciation are extended to John H. Callahan and Gary J. Klopf for lessons learned which extend far beyond the scope of research.

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iv TABLE OF CONTENTS

I. INTRODUCTION... ... 1 II. EXPERIMENTAL... ... 5 III. .\ESULTS a n d discussion... 7

A* PrtEMIX BUnNEnS. •»•••••••«••••••••••••

1. FT.AMR CONDITIONS...

2. ASPIRATION RATE... ... 3. IMPACT BEAD POSITION...

SURFACTANT GHAivGE...

5. SURFACE TENSION...

B. TOTAL CONSUMPTION BUrNErS... 36

IV. CONCLUSIONS AND FUTUnE rESEArCH... 45

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' :.f A; -t: ■;% vs-:';.:: ;:j;: -V E.: ':■H‘il':"W ■ K f 8- S' :15:: IIS A:';v/'f ^; A (rut deal of study has boon performed on solvent offooto in flono atomio epeotroacopy (PAS). Moot work hoo involved tho addition of orgaiio compounds, which lower tho ourfaoo tension of tho solution, resulting in a finor aoroool gonoratod during neb- lioation and more officiont flam# proooosoo. Organic additives can also affoot tho apparent fuel nixturo of tho flono (i).

A noro liaitod volune of study has concornod tho role of sur­ factants in suoh a oapaoity. Tho eonpatibility of surfactants with, and thoir inherent ability to roduoo tho surfaoo tension of. aqueous systems would load one to prodiot enhanoed sonsitirity in PAS determinations with surfaotant additives. Moot reported studios (2.3) have used nonionic surfaetants in total consumption omission spootrosoopy with no rsportod suoeoss. despite a reduction of surface tension (from 73dynes/em* for water to 30-38dynee/cm* for Triton X-100). The inactivity of surfactants in this ease has been attributed to tne non-equilibrium situation existing at the total consumption nebuliser-bumer tip (A). This point was con­ firmed through surfaotant diffusional oonsideratiens as presented by Kornahrens (5). An estimate of 10ms was reported for the dif­

fusion of the dodeeyl sulfate anion to the droplet surface. With­ in the constraints of the premix chamber, surfaotant redistribution is likely to occur as droplet lifetimes are typically iOO-AOOas (6) By the nature of its design and operation, the total consumption burner is incapable of allowing sufficient time for this reorien­ tation of the droplet surfaoe.

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frao-■■ ... . I.:.,:.,-.,,,.

••■'vm- ■■■ :|#S'v: ■;

tion of i l l pas application*• oyn i n t s t i l l o s s i i i r

tion of t&i oroaixod« laainar flaaa# In tha n o m t tmat* Jifraiial*m.m. *$WW . WMmmmmw ^ P a 1 * ^ 9 * - w | M V ^ | f Pl p V

worxara neve raportas oHtntxioni ox m h i m w nnuiivity n w

anionic aurfaotanta In pranixad flansa. Kodana, at al. (7) found ohroniun absorption to bo doubled at aodiua dodaoyl aulfata (SDS) was addod In oonoantrationa up to tha oritioal aiealla oonoantra- tion (CMC), with oonatant anhaneoaont at higher concentrations. Zn a later atudy, Kodaaa and Miyagawa (8) raportad tho production of a finar aaroaol when aurfaotanta waro praaant and related tho obaarvad anhanoaaant to inoroaaad atoaiaation offiolonoy duo to snaller droplata. Tha laval of anhanoaaant waa alao aaan to da- pond upon tha analyta, varying invaraaly with analyta aanaitivity.

Vanablo and Ballad (9) latar raportad aiailar roaulta with ooppar art niokol in tha proaonoo of 80S. A alight dssensitlsa- tion waa raportad in tha dataraination of ooppar in tho prMonoo of a eatienie aurfaotant, tetradeoylpyridiniun broaido.

Provioua work in thia laboratory (5) ahewod a aanaitiaation of ooppar abaorption (uaing a proaixad flato) by tha addition of anionic aurfaotanta up to tha CMC with a alight daoraaao in anhan- eamant at highar oonoantrationa. Cationio and nonionio aurfac- tanta wara found to hava littla or no affaot. A raportad dapan- danoa upon tha oxidant flow rata nay ba attributad to ita affaot on droplat diatributiona. Drawing on tho aaroaol ionie redistri- bution (AIR) thaory of Borowieo, at al. (10), a oharge-dependent thaory waa propoaad for tha obaarvad aanaitiaation. Tha AIR nodal of Borowieo notaa that upon ganaration of an aaroaol, tha watar- air intarfaoa ia boliavad to undergo a raoriantatlon prooaaa re­ sulting in tho alignnant of watar nolaoulaa with thair oxygon

. MmSSw\: | ;s§

__ < -'

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atoms faoing outward (ll). Aa a result of polarisation effects# an olactrioal double layer la established oapabla of attresting a diffuao layer of cations through a laytr of aniofta* fho aiAan* eanont aoohaniaa propoaod by Komahrons, at al. la an axtanaion of tha Alii thaory in which tha hydrophobic surfactant aolaculas ao- cumulata at tha droplat surfaea (due to surface activity) and are oapabla of.attracting ions through oharga intaractiona with their polar haad groups. A oonoantration of tha analyta into smallsr droplata occurs via a stripping action during tha braak up of larga droplata in tha nabulisation proeass. Tha drop off in enhancement observed above tha GhC was attributed to tha analyta binding to tha micelles within tha bulk solution, reducing tha surface concentra­ tion ans subsequent stripping affect.

This study serves as an extension of tha earlier work with a particular eaphasis on improving and oharaoterlsing tha parameters affecting tha reproducibility of tha enhancement of oopper determin- nations. Factors to be studied include flame compositon, sample uptake rata, impact bead position, and observation height.

Tasting for AIR affects in premixed flame amission speotros- copy was also undertaken. Because AXh is a nabulisation phenome­ non, it should be expected in any premixed flame method. Exten­ sion to emission should be straightforward, but has not yet been reported. A successful outcome should conoborate the AIR model.

The final objective of this study was to assess the effect of surfactant charge, with respect to the Ain model, in total consump­ tion emission speotrosoopy. Because AXK in premixed flames relies on preferential sampling of analyte-enriohed small droplets, and since there is no similar drop-aise bias with total consumption

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burners, the

AIR

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woro

possible, including iaproveaent la rtoaiseticn

efficiency by

o reduction in droplet siae or a change in flaws

ohoniatry

(duo to the fuel-like hydrocarbon nature of the eurfactant additives).

These affeota should hava charge and ooncantration dependences different ffrosi those observed in studies with prefixed fleasa.

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5 II. SXPSKXkENm

riaggenti. All copper solutions were prepared from a lOOOppm stock solution, reagent grade Cu(NOj) 3H20 (Allied Chemical Co.), SOS (MCB), Triton X-100 (TX-100» Sigma), and cetyltrimetylammonium bromide (CTABi Sigma) were used without prior purification. All glassware was triply rimed with distilled, deionised water prior to use. Solutions were made with distilled, deionised water trea­ ted in a Millipere filtration system. Solutions were generally used between one and 24h of preparation after mixing. Xn a sepa­ rate study, solutions were shown to exhibit no time-dependent cha­ racteristics over a period of several weeks.

Procedure and Apparatus. A Perkin-Blaer 4000 atomic absorption spectrophotometer was used with a long path, premix burner and an air-acetylene flame for all absorption studies (except where noted). All such studies were corrected for background absorption using a deuterium lamp. While this instrument was equipped with a variable

rate nebulizer for use in the uptake rate study, investigation of impact bead position was limited to a single position by the design of the manufacturer.

A GCA/tlcPherson Model EU-703-70 AA/AE/AF spectrophotometer was utilised in all emission studies. The McPherson set-up was equip­ ped with one of two Varian Techtron long path burners for premixed, laminar flames (a 5cm slot with nitrous oxide-acetylene for A£ work, and a 10cm slot with air-acetylene for AA to provide instrumental comparison with the Perkin-Elmer). This set-up also employed a varialbe rate nebulizer and an adjustable impact bead which made

parametric studies feasible. Total consumption emission studies used the same McPherson spectrophotometer equipped with a Beckman

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6 hydrogen-oxygen atomiser-burner. Surface tension measurements Mrs performed on a du Nuoy tensiometer with a platinum ring calibrated against standard solutions of water and acetonitrile

(73.05 and 29.30dynes/cm , respectively).

Sensitivity was defined to be the slope of a best fit, least squares linear calibration ourve consisting of signal values for six Cu2+ concentrations evenly spaced between 0 and lOppm. Para­ metric optimisation was performed with solutions containing sero and 2sfc SOS. Systematic error and instrumental drift was minimi­

zed by randomly sampling solutions of varying copper concentrations and a given SDS concentration. Xn the case of surfactant concen­ tration studies, sets of solutions at a given surfactant concentra­ tion were run in random order.

Enhancement was calculated as followst

(elope)8Urf - (slope)0

% Relative Enhancement » .... .... X lOOf (slope)0

where (slope)#urf* 'the slope of a ealibration ourve for solutions containing a given concentration of a given surfactant, and (slope)0 - the slope of a calibration curve for solutions containing no sur- faotant. All determinations (absorption and amission) were perfor­ med et the 32A.8nm line.

In the flame condition studies, end all remaining determina­ tions, gee flow rates were measured using Matheson flowmeters (ro­ tameters). Flows measured were corrected for density and pressure.

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7

III. nESULTS AMD DISCUSSION Premix Burners.

Flame Conditions. Due to the influence of oxidant flow rates on the aerosol droplet site distributions (5)i * single oxidant flow rate was maintained throughout the study and the fuel flow rate was increased to provide higher fuel percentages. Figure 1 illustrates the dependence of an AA determination of Cu on the flame composition, using 0 and 2m& SDS. Two important features are evident. First, there is clearly an enhancement of sensiti­ vity with the addition of SDS. This is consistent with the fin­ dings of Kornahrens and Kodama. confirming a real change in sen­ sitivity (represented by the slope of the calibration ourve). and not simply a change in interoept. Secondly, the sensitivity

(with or without surfactant) does not vary significantly with per­ cent fuel until conditions sure sufficiently fuel rioh to create a luminous flame, where sensitivity and enhancement decrease

sharply. The possibility of aerosol dilution by the higher total

gas flows at such conditions is not a likely possibility as sen­

sitivity dropped nearly 14* when percent fuel was increased from 16.7* to 21.5*. representing an increase in gas flow of only 6*. A dilution effeot would be expected to produce a more gradual change with increasing flow. A second possible explanation oould be an increase (with increasing fuel) of vaporisation interfer­

ences. However, this should be accompanied by changes in verti­ cal flame profiles. Beoause there is no detectable change in the atom distribution within the flame, this alternative is also un­ likely. The most probable explanation may therefore be spectral interference from flame luminosity. The wide range of flame

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eon-Figure 1. Optimization of Air-Acetylene Flames i AA Air Flow Kates 13*5 l/m

Uptake Hates 4,2 l/a O — 0 aM SDS

O — 2 aM SDS

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S E N s m v rr r ( a u / p p h )

*1

0

0 .7 6 0 ,8 2 0 ,8 8 0 .9 4

0PT/ENHRNCEMEKT IN RIR-C2H2 FUMES

9.00 11.00 T--- T--- T---13.00__ 15.00 17.00T~

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10 ditione over which the sensitivity remains relatively constant and high has been partly attributed to the low dissociation en­ ergy of copper oxide (12,13). In general, air-acetylene flame composition appears to have little effect upon the magnitude of enhancement except in luminous flames, where overall sensitivity is low. This is consistent with the Ain model, because Ain is a nebulisation phenomenon and would not be expected to exhibit a dependence upon flame composition, fieoause reproducibility should be improved in leaner flames (sensitivity appears to be nearly independent of percent fuel from 10£ to 18%) the leanest stable flame composition was used (approximately 12% fuel).

results of a similar experiment performed with a nitrous oxide •acetylene flame used in emission studies are given in figure 2. The level of enhancement is roughly constant throughout the study, with relatively large random deviations. The observation of an overall optimal flame composition in the nitrous oxide flame may result from temperature variations or possible formation of car­ bonaceous compounds forming in fuel-rioh flames. Emission studies exhibit a greater sensitivity to temperature as atoms must be ex­ cited following atomisation. The existence of an optimal flame condition would appear to indicate a maximisation of flame tem­ perature resulting in the greatest energy transfer to the analyte. Baded on this information, future AE studies employed nitrous oxide -acetylene flames with 29-3IJ* fuel.(versus 1?> as stoichiometric). Aspiration Kate Effects. When investigating the effects of so­

lution uptake rate on sensitivity, optimal flame conditions were ohosen consistent with the findings reported above. Beginning with the lowest aspiration rate, sensitivities were measured with

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Figure 2. Optimisation or Nitrous Oxide-Acetylene Planes t AE NgO Plow Kate a 9*9 l/s

Uptake Kates 3*^ al/a

© — 0 m SOS

Q — 2 a§. SOS

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S E N S I T I V I T Y ( f l N P S / P P M ) * 1 0 0 . 0 2 0 . 0 3 0 . 0 4 0 , 0 3 0 , 0 6

B

o

0PT/EHHRNCEMENT IN N20-C2H2 FUMES BE

f + + B + -41) O ^0.00 13.30 17.00 2&.50 24.00

PERCENT FUEL

8

m — y | -O 31.00 34.30 36.1)0
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13 0 and 2m& iDS and tha uptake rate wae than stepped through the range of study, roughly 1 to 8ml/m. Figures 3 end A illustrate the results of this experiment for AA and AS determinations, re* speetively. .Several trends are evident. First, there is a non­ linear relationship between sensitivity and uptake rate. This occurs in both studies regardless of surfactant concentration, indicating an overall transport phenomenon. Secondly, allowing for random experimental deviations, the relative enhancement does not appear to exhibit any dependence upon uptake rate.

There is one noteworthy difference between AA and AS results. Xn contrast to the AS study, the AA investigation exhibits no opti­ mal uptake rate in terms of sensitivity. This may be attributed to the improvement of traneport efficiency by an auxiliary air flow found in the Ferkin-Blmer (AA), but not in the GCA/feeiteereea

(AB)(1A). Auxiliary air is a fraction of the total oxidant flaw which entere the gas stream through the side of the spray chamber, rather than through the nebuliser. The effects of auxiliary flews are mixed. While decreasing gravitational settling losses, auxi­ liary air increases losses through coalescence. When choosing am aspiration rate for further studies, Howsrth, et al. (15) found rates of 2-3ml/m provided the best compromise between sensitivity, flame stability, and sample usage. Zn keeping with these findings and the results obtained here, a slightly higher range of rates, 3-5ml/m, was used. This was preferred beoause the variation of sensitivity with uptake rate over this seleoted range was smaller than that over the range suggested by Howarth.

Beoause many variables are involved in the nebullsatlan and transport of the sample to the flame, the explanation of their

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ef-Figure 3. Optieisatiaa of Uptalre Hate in M r ^ C ^ M r Flea Kates l).) l/e

C^l2 Floe Kates 1*5 M * (15.0J&)

0 ~ O aK »S □ — 2 4| SOS

(20)
(21)

Figure Optimization of Uptake Kate in N„0-C_H„ Flames« AE N_0 Flow Eatet 9.9 l/m C_H2 Flow Katet 3-7 l/» (27.2*) O — 0 mN SDS 0 — 2 mM SOS ■f — nelative Enhancement Ov

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18

fects becomes complicated and oftan tvarlapping. For example, the solvent is able to axart an effect upon tha flaaia. Howarth, at al. (15) propoaad an increased oxidising anvtrawiant within tha flame aa oxygen concentration increases with the introduction of an oxygen-eentaining solvent. This would load to improved sensitivity with the air-aoetylene flame, as tha fuel percentage would be decreased (see fig.l). However, suoh effects should be minimal in this case, because the amount of solvent-derived oxy­ gen reaching the flame is small with respect to the gas flow rates, and because the determination is relatively insensitive to changes in composition in the region of study. A different solvent effeot which might be more important here is the saturation of the gas stream by the solvent. Dependent on the vapor pressure of the sol­ vent and temperature of the gas mixture, saturation generally oc­ curs at uptake rates exceeding 3ml/m (16), This results in dimin­ ished vaporisation and therefore, formation of larger droplets. This in turn inoreases collisional and gravitational losses (see below), decreasing the overall mass transport efficienoy.

Table One shows how the sample volume reaching the flame varies with the observed uptake rate. The volume of sample in the flame was determined by the difference between measured uptake and the volume of waste collected.over an extended period of sample introduction. The reported volume efficiency is the percent (vol) of sample which reaches the

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Table One. Transport Efficiencies in Premixed Burner**. Air Plow rtatei 11.3 l/B

C2^2 ^low Kate* 1*7 l/»

ntMOTTrod nr»air« i.ate. al/m i m SDS) Sample teaching Fla... «l/n Transport Kfficlency(»)

2.66 (0) 0.46 17.3 2.7* (4) 0.46 16.8 2.86 (2) 0.47 16.4 4.76 (4) 0.60 12.6 5-32 (2) 0.58 10.9 5.66 (0) 0.54 9-5 7.19 (2) 0.47 6.5 7.46 (0) 0.51 6.8 >o

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Figure 5 Voluae Transport Efficiency versus Uptake Rate

Air Flow Rates

C2*I2 Flow Rates

o — 0 a|| SDS 0 — 2 ail SDS + ~ 4 aN SDS 11.3 l A 1.7 !/■ (13.Q*) M O

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TRRNSP0RT EFFICIENCIES IN PREMIX BURNERS

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1.00

2.00

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(27)

flute. The same data is summarised in figure

5* In

this limi­ ted study (which includes results with 0. 2, and 4m|i SOS), it is clear that the surfactant dos not affect the uptake efficien­ cy, since a single curve appears to encompass all data (fig.5)•

With a variable rate nebuliser, the oxidant flow rate is in­ versely related to the uptake rate (15)• The initial increase

in signal with uptake rate may then be the result of a concentra­ tion of the sample within the gas stream. An eventual increase in large droplet populations with decreased nebulising gas flow could reduce evaporation efficiency and explain the plateau and slight decrease in signal at high uptake rates. Collisions! los­ ses may also be involved in the decreased sensitivity at high as­ piration rates, as the collisional frequency is proportional to the square of the droplet density (number of droplets per unit volume). An extension of collisional processes encompasses the possible loss of signal in AE due to collisions occurring within the flame. As more droplets reach the flame, there may be a "quenching" of excited atoms through a collision with a droplet or desolvated particle, reduoing the signal.' For elements sensi­ tive to vaporisation interferences (i.e. Ca) there may thus be an optimum flow rate representing a compromise between sensitivity and interference effects.

Depending upon the gas flows encountered, there are two other types of losses which should be consideredi gravitational set­ tling and impaction. At high uptake rates, lower flows can reuult in longer transport times. This, combined with larger droplet sites due to coalesoence resulting from collisions at high aero­ sol densities, increases losses due to gravitational settling (17)

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On the other hand, high gas flows inpart greater momentum to the aerosol and losses increase through collisions with the spray chamber. Both processes tend to shift droplet distributions to smaller diameters, although they are brought about by opposing conditions. In a study with a dual concentric spray chambered ICP system. Browner (17) showed that despite a decrease in neb* ulisation efficiency with uptake rate, the useful mass transport rate, defined as the flow of analyte contained in droplets con­ tributing at least 10Jt to the signal, remains relatively constant. This important since ICP and premix FAS systems are very similar with reapeot to sample transport.

Impact Bead Position. A further consideration must be made when using an impaction surface, such as a mixer paddle or impact bead, as was employed in these studies. While removing large droplets, the bead also serves to provide secondary fragmentation of the aerosol.(The efficiency of such surfaces is improved in the absence of auxiliary air flows (14). This may be attributed to increased turbulence as auxiliary air tends to flow around the walls of the spray ohanber before mixing with the aerosol.) In figure 6 one sees the effect on sensitivity of positioning the im­ paction bead. While there appears to be an optimal position with respect to sensitivity, the observed enhancement appears to exhi­ bit no such dependency. A similar optimisation was reported by Kouth (18) and expained by improved droplet sise and number reac­ hing the flame. In further studies a position of 1.25mm was used. Surfactant Charge Effeots. Figures 7-10 dearly illustrate the dependence of the sensitisation meohanism on surfactant charge. As would be expected, figs. 7 and 8 show a similar trend in

(29)

Figure 6 • Optimization of Impact Bead Position in AE

H^O Flow Hates 9*9 !/■

CgHg Flow Hates 3-7 l/« (27.2*) Uptake Hates Jt.O ml/e

O — 0 am SDS □ — 2 aM SDS

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(31)

Figure 7 • Surface Tension and Absorption Effects of SDS in AA Air Flow Kates 14.5 1/m

C^Z Flow ****** 1 .5 1/m (9.4*) Uptake Rates 2.9 nl/n

0 — Perkln-Ebeer 0 — GCA/fecPkerson H ---Surface Tension

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Surface Tension and Emission Effects of SDS N^O Plow Katei 9.9 l/m

0 ^ 2 Floir ***•• 3*7 1/® (27.29*)

Uptake Katet 5*1 ml/m 0 — Relative Enhancement

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6

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30 cement with SDb concentration for the absorption and emission an­ alyses. Sensitisation is observed to increase to a maximum with increasing SD5 monomer concentration, followed by a decrease in the effect with the formation of micelles upon reaching and ex­ ceeding the CMC. The magnitude of this post-CMC effect depends on the degree of association of the analyte with the micelle, which has been shown previously to be more complex than merely a charge effect (19).

The hotter, higher velocity, nitrous oxide-aeetylene flame utilised in emission studies yielded a maximum enhancement nearly 6& greater than the air-acetylene flame employed in atomic absorp­ tion studies. The droplet else distribution has been shown to in­ fluence the lateral distribution within the flame. A lateral nar­ rowing of the aerosol distribution has been observed with increa­ sing solute concentrations, resulting from larger particles and less lateral diffusion (20). Such an effect is not generally ob­ served in the air-acetylene flame, as gas velocities are typically 2-3 times lower than those incurred with the nitrous oxide bumei'

(due to a faster burning velocity). Unfortunately no evidence of this phenomenon could be detected in the lateral profiles measured with various surfactant concentrations. As of this time, a suf­ ficient explanation has not been found for the greater seneitisa- tions observed with the nitrous oxide-aoetylene flame over the air- acetylene flame. A combination of fuel mix and AIR effects is possible.

As expeoted, although only briefly reported by Venable and Ballad (9), the addition of a oationic surfactant, CTAB, desensi­ tised the analysis. With a positively charged surfaoe (brought about l>y the CTA+ cation), the analyte is repulsed from the sur­

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31 face. Consequently there is depletion of the analyte from the small droplets generated from the surface material upon nebulita- tion, as described by the Ain model. Upon formation of cationic micelles at and above the CMC, the precision of the analysis is seen to decrease substantially (see fig.9). This may be attributed to opposing charge repulsion effects, as the analyte is not only re­ pulsed from the surface, but also from the bulk region by the mi­ celles. Another possibility is the increase in solution viscosity with surfactant concentration and possible effects on uptake rate. Surface Tension Effects. Surface tension was studied indepen­ dently from Al.i effects by the addition of TX-100. Figure 10 il­

lustrates the effect of decreased surface tension in premix AS. Although random scatter appears within the data, the overall mag­ nitude of the effeot is seen to be small. Some of this apparent

insensitivity to surface tension effects may be due to the faot that copper is atomised very efficiently in air-acetylene (21) and nitrous oxide-acetylene flames (13).

A deorease in surface tension has been shown to be accompani­ ed by a lower mean droplet diameter (8). This effect can be indu­ ced by the addition of surfaotant, in whioh case it is maximised at concentrations at, or above, their CMC. Decreases in droplet diameter also allow for more efficient production of dry salt par­ ticles as evaporation efficienoy inoreases due to the inverse pro­ portionality between surface area per unit mass and particle diam­ eter (22). As a result, reaction with the flame occurs faster as the aerosol has a greater surfaoe area. This effect is likely to be limited, in most cases, by saturation of the gas stream. For easily atomised elements saturation is not critical as large

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drop-Figure 9 • Surface Tension and Emission Effects of CTAB in AE Flow Katei 7*6 l/m

C^i2 Flow Kate* 3.7 l/m (30.9*)

Uptake Kate* 5*1 ml/m O — Kelative Enhancement 0 - -Surface Tension

Error bars represent the standard deviation of the measurement as evaluated after three trials.

(38)
(39)

Figure 10. Surface Tension and Enission Effects of TX-100 in AE *2° Flow Kmt#* 7.6 1/m Plow 3.4 l/* (30.9?fc) Uptake Rates 5*0 ml/m © " R e l a t i v e Bnhancesent O — Surface Tension

Errcnr bars represent the standard deviation of the aeasureaent, as evaluated after three trials.

(40)

§

YX-lOO SUffUCt AND EMISSION EFFECTS

&

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00

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(41)

36

lets may contribute to the signal. Aouth (18) has shown the aero­ sol median droplet diameter increases upon passage through the burner slot. A point of further study is the opposing effects of coalescence within the burner slot and droplet diameter reduction by the addition of surfactants. Despite the positive effects of

reducing surface tension as discussed, their role in a sensitisa­ tion of the determination appears to be much smaller than charge considerations.

Total Consumption Burners

Flame Conditions. Based on premix results, it was assumed the addition of &M would not affect optimum conditions, so optimisa­ tion experiments were performed with no SD5. When determining opt­ imal flame conditions in the hydrogen-oxygen total consumption burner, the oxidant flow rate remained fixed to provide a constant solution uptake rate. The best sensitivity was obtained with fuel -rieh conditions, see figure 11. This was attributed to the bur­ ning of excess fuel with entrained air. Threu^wvt

tiie remaining studies with this set-up a burning mixtmre with Shout 75% fusl mas used (slightly richer than the sfadnilpastry).

The metal consumption burner was met siptppsi with a variable rate nsbuliser so uptake rede could net be otudrted independent of flaao composition. The gas flaws ussd, J.H/b of C2 and 9.31/kHg, were ohosen on the bands of optimal flams composition osid signal

stability (dependant upon sufficient sample delivery), nesulta of Foster and Hums (3) Indicate that independent variation of uptake rate affects flams temperature sensitively. This is particularly important with clcmcntc characterised at high energy lines, as sen* sitivity for these determinations was optimised at lower rates.

(42)

Figure 11. Optimisation of Hydrogen-Oxygen Flames i AE

Total Consumption

0 2 Flow Rates 5 . 8 l/» Uptake Rates 1 * 9 5 a l/a

(43)

S

E

N

S

I

T

I

V

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T

Y

(flN

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/P

PM

)

*1

0

0.

04

0.

08

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0PT. IN H2-02 FLRMES TC RE CsJ m-o o o © 0 0

8

% 0 , 0 0 54.00 58.00 62.00 66.00 70.00 74.00 78.00

PERCENT FUEL

82.
(44)

39

Since copper has a much higher excitation energy than the alkali metals studied by Foster and Hume, the optimum uptake rate would probably be impracticably low, regardless of these

considerations, a sound assessment of Alit under the stated exper­ imental conditions can be made.

At the low uptake rates encountered here, 0.5-0.8 nl/m, the expected signal should be proportional to the solution flow (23). Assuming laminar sample flow through the uptake capillary (as des­ cribed by the Hagen-Foisseuille law)(23), the nebulisation rate should be inversely proportional to the solution viscosity. Ad­ ditionally, the Nukiyama-Tanasawa equation (24) for estimating the mean droplet diameter of such aerosols, predicts increasing sise with solution viscosity to a small extent.

Pungor and i.iahr (23) also predict improved dlspersity of the aerosol and subsequently more efficient emission with decreases in surface tension. The Nukiyama-Tanasawa equation offers no firm predictions on the effects of surface tension. As discussed in the introduction, surfactants must diffuse to the surface to ex­ ert an influence on surface tension, and the time scale of nebu- liaation in the total consumption burner may not allow for suoh diffusion. In fact, the data presented in figure 12 shows no clear relationship between surfactant concentration and sensitivity or resulting equilibrium surface tension, indicating that, indeed, equilibrium conditions do not apply.

This suggests that the sensitivity enhancement induoed by SOS (figure 13) is not attributable to the decrease in surfaoe tension as no similar trends were obtained with solutions of TX-100 or GTAS

(45)

Figure 12. Eaiaaion Efftcta ot TX-100 and CTAB in AB Total Consumption

02 Flow Kate* 3.1 1/m

H2 Flow Katai 9.3 l/» (75-0*) Uptake Katai 0.81 al/a

O — TX-100 (Two trials) □ — CTAB

■a

(46)

8

TX-100 CTflB EMISSION EFFECTS IN TC

(47)

Figure 13 Surface Tension and Eaission Effects of SDS in AS fetal Consuaption

02 Flow Kates 3.1 1/m

H2 Flow Kates 9*3 l/* (75.OJ^) Uptake Kates 0.78 ml/m

Q — helative Enhanceaent 0 — Surface Tension

Error bars represent the standard deviation of the neasureaent, as evaluated after three trials.

(48)

U.00

2.00

4.00

6.00

8.00

10.00

12.00

14.00

QWC SOS CMN0L)

(49)

ascribed to possible increases in flans fuel, noting the simila­ rity bstwssn eurvs in s 11 and 13. SOS is present in approximately a 14-fold excess (w/w) with respect to TX-100 and 42 tines more concentrated than CTAB. In a limited study, TX-100 produced levels of enhancement ocoprable to those observed with SOS, when present in similar amounts (by weight, relative enhan­ cement of .about 23?» for 7>4m& TX-100). Ain does not appear to exist in the total consumption burner, as evidenced by the dif­ ference in enhancement dependence upon SOS concentration. Ho de­ crease is noted at concentrations above the CkC in fig. 13*

44

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IV. CONCLUSIONS AND FUTURE RESEARCH

Fran the parametric study conducted with and without surfac­ tant, little dependence of the enhancement mechanism was noted* with the exception of conditions where the overall determination decreased (i.e. luminous air-acetylene flames). Some of this in­ sensitivity to experimental parameters has been attributed to the element studied here and its apparent freedom from most interfe­ rences encountered in AS. Additionally, the dependence of the magnitude of the effect, upon the flame used must be explained.

Confirmation of surface tension effects and the non-applica­ bility of AIR to the total consumption burner were observed. A fuel effect was proposed for an observed increase in signal when high concentrations of the organic surfactants were present, while no charge dependence was noted. Future work in this area should include a study of different types of surfactants present in con­ centrations adding equimolar- amounts of potential organic fuel.

Finally, the dependence upbn surfactant charge was also con­ firmed with cationic surfaotants, with a proposed repulsion-based theory on the concentration dependent desensitisation observed.

Further experimentation is needed not only in researching the magnitude of the effect with different analytes, but also within

the more complex matrices commonly encountered in the typical FAS determination. The fundamental study of aerosol generation and transport with respeot to the addition of surfaotants remains a field for study.

(51)

V. REFERENCES

1. Pungor, E. , "Flame Photometry Theory," Van Noetrend, London, 1967.

2. Lockyer, h.i Scott, J. B.i Slade, S. Natura(London) 1961, 189. 830.

3. Postar, W. H.j Hume, D. N. Anal. Cham. 1959. 21. 2028.

A. Dean, J. A., Rains, T. C., Eds., "Flame Emission and Atomic <■>', "orption Spectrometry," Marcel Dekker, New York, 1969, Vol. 1 (Theory).

5. Komahrens, H.| Cook, K. D.i Armstrong, 0. W. Anal. Cham. 1982, 5£, 1325.

f. Browner, a. F. Georgia Institute of Taohnology, Atlanta OA, personal communication, 1981.

7. Kodama, M.» Shimitu, S.i Sato, M.j Tominaga, T. Anal. Lett,, 1977, lfl, 591.

8. Kodama, M.» i«iyagawa, S. APli,*, Qh«1U 1980, 51, 2358. 9. Venable, R. L.i Ballad, R. V. Anal. Cham. 1974, ££, 131. 10. Borowiac, J. A.i BoOm, A. W. i Dillard, J. H.i Crasser, M.

S.| Browner, n.F. Anal. Cham. 1980, 52. 1054.

11. Loeb. L. B., "Static Electrification," Springer, Berlin, 195s pp. 61*80.

12. Fujiwara, K. 1 Haraguchi, H.i Fuwa, K. Anal. Cham. 1973. j£, 743.

13. Fassel, V. A.i nasmuson, J.’Q.i Kniseley, R. N. 1 Cowley, T. 8* Sneotroohlm. Acta 1970, 252. 559.

14. Crasser, i4. S.i Browner, a. F. Annl. Snaa. 198O, 384. 15. Howarth, H.i WcKentie, T. H.i aouth, H. w. Anal. Snaa, 1981,

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21, 164.

16. Stupar, J.» Dawson, J. B. AbbIi flBti 1968, 11, 1351*

17. Browner, K. F. i Boom, A. W.| Smith, D. D.Anal. Chea. 1962, 14, 1411.

18. nouth, M. W. Anal. Spec. 1981, H, 170.

19. Ziaalekl, H. i Cherry, W. ri. J. Am. Chen. Soe. 1981, 1£1, 4479 20. L'vov, B. V.» Katskov, D. A.» Kruglikova, t. P.i Polaik, L.

K. Saaetrochlm. Aeta 1976, Hfi. 49.

21. Willie, J. B. Saaotrochin. Aota 1971. 177.

22. Willis, J. B. Saaotrochla. Acta 1967, 22A> 811. 23. Pungor, £.1 tiahr, h. Tatawta 1963, U2« 537.

24. Nukiyama, S.| Tarasawa, Y. Trm«. Soe. hach. Ena. Japan 1939

References

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