Chapter 7
Simultaneous Collection of Particles and Acidic Gases for Tracing Emissions from Coal-Fired Power Plants
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Michael E. Kitto and David L. Anderson Department of Chemistry and Biochemistry, University of Maryland, College Park, MD 20742
Particulate and gaseous atmospheric components have been sampled using a multiple-filter system. A Teflon filter for particle collection preceded four LiOH/ glycerol treated Whatman-41 filters i n a stacked filter arrangement. Up to fifty elements were detected on the p a r t i c u l a t e filter, while ten elements (B, N, S, Cl, As, Se, Sb, Br, I and Hg) were observed on the base– treated filters using the combined techniques of PGAA, INAA and IC. The base-treated filters proved to be very e f f i c i e n t c o l l e c t o r s of the a c i d i c gas-phase species, but apparently allow some elemental and organic species to pass through as shown by studies with activated charcoal-impregnated filters. A p p l i c a t i o n of observed concentrations of atmospheric p a r t i c l e s and a c i d i c gases are compared to the results predicted by a hybrid receptor model. 7
In t h i s study we have employed the s i m u l t a n e o u s c o l l e c t i o n of a t m o s p h e r i c p a r t i c l e s and gases f o l l o w e d by m u l t i e l e m e n t a n a l y s i s as an approach f o r the d e t e r m i n a t i o n of s o u r c e - r e c e p t o r r e l a t i o n s h i p s . A number of p a r t i c u l a t e t r a c e r elements have p r e v i o u s l y been l i n k e d to s o u r c e s ( e . g . , V to i d e n t i f y o i l - f i r e d power p l a n t e m i s s i o n s , Na f o r marine a e r o s o l s , and Pb f o r motor v e h i c l e c o n t r i b u t i o n ) . R e c e p t o r methods commonly used to a s s e s s the i n t e r r e g i o n a l impact of such e m i s s i o n s i n c l u d e c h e m i c a l mass b a l a n c e s (CMBs) and f a c t o r a n a l y s i s (FA), the l a t t e r o f t e n i n c l u d i n g wind t r a j e c t o r i e s . With CMBs, s o u r c e - s t r e n g t h s are determined (1) from the r e l a t i v e c o n c e n t r a t i o n s of marker elements measured at e m i s s i o n s o u r c e s . When enough sample a n a l y s e s are a v a i l a b l e , c o r r e l a t i o n c a l c u l a t i o n s from FA and knowledge of s o u r c e - e m i s s i o n c o m p o s i t i o n s may i d e n t i f y groups of s p e c i e s from a common source type and i d e n t i f y p o t e n t i a l marker elements. The source c o m p o s i t i o n p a t t e r n s are not n e c e s s a r y as the e l e m e n t a l c o n c e n t r a t i o n s i n each sample are n o r m a l i z e d to the mean v a l u e of the e l e m e n t . R e c e n t l y a h y b r i d r e c e p t o r model was proposed by Lewis and Stevens (_2) i n which the d i s p e r s i o n , d e p o s i t i o n , and c o n v e r s i o n c h a r a c t e r i s t i c s of s u l f u r s p e c i e s i n p o w e r - p l a n t e m i s s i o n s 0097-6156/87/0349-0084$06.00/0 © 1987 American Chemical Society
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.
2
7.
KITTO AND
ANDERSON
Tracing Emissions from Coal-Fired Power Plants
are r e l a t e d to a f i n e p a r t i c u l a t e t r a c e r element ( e . g . , S e ) . In t h i s s t u d y , we have t r i e d to extend t r a c e r t e c h n i q u e s f o r c o a l - b u r n i n g u t i l i t y e m i s s i o n s to i n c l u d e gas-phase elements, and to r e l a t e r e c e p t o r measurements to the h y b r i d r e c e p t o r model, as m o d i f i e d by Gordon and Olmez Ç3). Mass b a l a n c e c a l c u l a t i o n s (4,_5) have accounted f o r o n l y 30-50% of f e e d c o a l boron i n the ashes, i m p l y i n g the r e s t was r e l e a s e d i n the gas phase. A n a l y s i s of s i z e - f r a c t i o n e d f l y - a s h by PGAA showed an enrichment of B, as w e l l as S and Cd, on the s m a l l e r p a r t i c l e s ( 6 ) , and r e c e n t s t a c k measurements of gaseous Β c o n c e n t r a t i o n s v a r i e d from 700 to 5000 yg/m a f t e r a 20:1 d i l u t i o n w i t h ambient a i r (7_). Fogg (8) has shown t h a t , based on the c h e m i c a l p r o p e r t i e s of boron compounds, the p l a u s i b l e gas-phase Β s p e c i e s i s B(0H)3, b o r i c a c i d . B(0H)3 t h e n p r e s e n t s i t s e l f as a p o s s i b l e gas-phase t r a c e r f o r S O 2 , as both s h o u l d have s i m i l a r d i s p e r s i o n and d e p o s i t i o n c h a r a c t e r i s t i c s , w h i l e B(0H)3 w i l l not undergo c h e m i c a l c o n v e r s i o n analogous to S O 2 to s u l f a t e . By s i m u l t a n e o u s l y measuring gas-phase B(0H)3 and S O 2 , and p a r t i c u l a t e Se and s u l f a t e c o n c e n t r a t i o n s at a r e c e p t o r s i t e , we are a b l e to t e s t the h y b r i d r e c e p t o r model w i t h t r a c e r s i n both phases.
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3
Experimental The sampling system was d e s i g n e d f o r e f f i c i e n t c o l l e c t i o n , h i g h f l o w r a t e s , and minimal a n a l y t i c a l i n t e r f e r e n c e s . The optimum s t a c k e d f i l t e r system c o n s i s t s of a T e f l o n - b a s e d ( Z e f l u o r or F l u o r o p o r e ) p a r t i c l e f i l t e r p l a c e d p r i o r to a s e r i e s of ^ L i O H / g l y c e r o l t r e a t e d Whatraan-41 f i l t e r s i n the a i r - s a m p l e stream. Our s t u d i e s have shown t h a t Whatman-41 p r e f i l t e r s are i n a d e q u a t e to the e x t e n t t h a t about 5% of some s p e c i e s ( e . g . , S, B r , I) may pass through the c e l l u l o s e matrix. The c h o i c e of Z e f l u o r or F l u o r o p o r e p r e f i l t e r depends s o l e l y on b l a n k - v a l u e p r e f e r e n c e s or a v a i l a b i l i t y . 'LiOH i s used as our a n a l y t i c a l t e c h n i q u e s are i n s t r u m e n t a l n e u t r o n a c t i v a t i o n (INAA) and n e u t r o n - c a p t u r e prompt γ-ray a c t i v a t i o n (PGAA) a n a l y s i s , t h e r e f o r e the use of NaOH or KOH would cause s e v e r e s p e c t r a l i n t e r f e r e n c e s and " n a t u r a l " L i c o n t a i n s enough *>Li to cause s i g n i f i c a n t n e u t r o n s e l f - s h i e l d i n g i n the sample. N o r m a l l y , a T e f l o n f i l t e r f o l l o w e d by f o u r t r e a t e d 110-mm f i l t e r s are c o n t a i n e d i n a s i n g l e open-faced p o l y e t h y l e n e f i l t e r h o l d e r w i t h an exposed a r e a of 75 cm^ ( F i g u r e 1). T y p i c a l f l o w r a t e s were 3.3 L / s , p r o d u c i n g a f a c e v e l o c i t y of a i r at t h e f i l t e r s u r f a c e of 44 cm/s and a r e s i d e n c e time f o r gases on each t r e a t e d f i l t e r of about 0.5 ms. A l t h o u g h they are s i m p l e and h i g h l y e f f i c i e n t , a n n u l a r denuders were not used because they were u n a v a i l a b l e when the sampling began and are o n l y now b e i n g d e v e l o p e d to accommodate h i g h e r f l o w r a t e s . A l s o , they r e q u i r e a d d i t i o n a l p r e p a r a t i o n , w i t h p o s s i b l e c o n t a m i n a t i o n , of the sample p r i o r to a n a l y s i s by n u c l e a r t e c h n i q u e s , whereas s t a c k e d - f i l t e r samples c o u l d be a n a l y z e d w i t h v e r y l i t t l e h a n d l i n g or p r e p a r a t i o n . In t h i s s t u d y the f i l t e r samples were h a l v e d , bagged i n c l e a n e d p o l y e t h y l e n e t u b i n g , and f i r s t a n a l y z e d by PGAA u s i n g an e x t e r n a l i r r a d i a t i o n f a c i l i t y c o n s t r u c t e d by our group at the N a t i o n a l Bureau of Standards (NBS) r e s e a r c h r e a c t o r ( 9 ) . PGAA p r o v i d e d d e t e r m i n a t i o n s of the elements B, S, and CI on the t r e a t e d f i l t e r s , and B, S, CI, S i , Cd and o f t e n o t h e r s on the p a r t i c l e f i l t e r s . For a n a l y s i s of s h o r t - l i v e d i s o t o p e s by INAA, the bagged samples were
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.
85
THE CHEMISTRY OF ACID RAIN
86
i r r a d i a t e d i n the NBS r e a c t o r f o r 5 m i n u t e s . Subsequent accumulation and a n a l y s i s of each sample's γ-ray spectrum were performed a t the NBS r e a c t o r , u s i n g a p r o c e d u r e s i m i l a r t o that d e s c r i b e d by Germani et a l . ( 1 0 ) . A f t e r 3-7 days of c o o l i n g the samples were r e - i r r a d i a t e d f o r 4 hours to produce i n t e r m e d i a t e - a n d l o n g - l i v e d (η,γ) p r o d u c t s , and two counts were performed at the U n i v e r s i t y of M a r y l a n d (^4 and ^12 hours a f t e r ~3 and ~30 day decay t i m e s , respectively). Ion chromatography a n a l y s e s of some of the o t h e r f i l t e r h a l v e s were performed at the NBS C h e m i s t r y b u i l d i n g to p r o v i d e a check of S and CI v a l u e s o b t a i n e d by PGAA and INAA, as w e l l as to p r o v i d e measurements of N0 .
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X
Results
and
Discussion
For a s e t of 14 f i l t e r samples taken i n C o l l e g e Park, MD d u r i n g May, June, and J u l y of 1984, 45-50 elements were r o u t i n e l y d e t e r m i n e d on the p a r t i c l e f i l t e r by the combined t e c h n i q u e s , and f o r the gas-phase t h e c o n c e n t r a t i o n s of S, C l , Br, I, As, Se, Sb and Hg (by IIMAA) and B, S, and CI (by PGAA) c o u l d be measured ( F i g u r e 2 ) . The average s a m p l i n g p e r i o d was about 3 days. The c o l l e c t i o n e f f i c i e n c y of the f i r s t t h r e e ^ L i O H / g l y c e r o l s t a c k e d - f l i t e r s ( s t a g e s 2-4) can be o b s e r v e d i n F i g u r e 3. In t h i s t y p i c a l sample (^800 m ), as f o r o t h e r s taken at v a r i o u s s i t e s , the f i r s t t h r e e b a s e - t r e a t e d filters c o l l e c t v i r t u a l l y a l l the a c i d i c gas-phase s p e c i e s . B l a n k or i n s i g n i f i c a n t l e v e l s are o b s e r v e d on s t a g e 5. The p e r c e n t a g e of the t o t a l mass of elements d e t e c t e d by t h i s system on the b a s e - t r e a t e d f i l t e r s were 78±11, 65±8, 75±26, 23±20, 5±3, 54±15, 0.5±0.8 and 91±3 f o r B, S, C l , As, Se, Br, Sb and I, r e s p e c t i v e l y . We do not r e p o r t Hg v a l u e s as the p a r t i c l e d a t a are u n r e l i a b l e due t o p o t e n t i a l l o s s e s during i r r a d i a t i o n . I t i s p o s s i b l e t h a t some of the measured g a s phase c o n c e n t r a t i o n i s due t o v o l a t i l i z a t i o n from p a r t i c l e s c o l l e c t e d on the p r e f i l t e r , and we are d i f f e r e n t i a t i n g between p a r t i c u l a t e and gaseous components w i t h an o p e r a t i o n a l d e f i n i t i o n . In t h i s s t u d y , the t r e a t e d - f i l t e r ( " a c i d i c gas-phase") c o n c e n t r a t i o n s w i l l i n c l u d e the a c t u a l gaseous components i n the a i r s t r e a m and a r t i f a c t s due t o v o l a t i l i z a t i o n from or r e a c t i o n w i t h the p a r t i c l e s on the p r e f i l t e r , and any v e r y f i n e p a r t i c u l a t e m a t e r i a l t h a t pass t h r o u g h the prefilter. A l s o , the " p a r t i c u l a t e " c o n c e n t r a t i o n i n c l u d e s a c t u a l p a r t i c l e mass p l u s any gaseous component adsorbed by the p r e f i l t e r . T h i s l a t t e r component i s p r o b a b l y v e r y s m a l l f o r T e f l o n - b a s e d f i l t e r s , but cannot be r u l e d out. 3
F o r the p a r t i c l e f i l t e r s we have determined enrichment f a c t o r s (EF) u s i n g Wedepohl's (11) c r u s t a l v a l u e s and the e q u a t i o n : EF
= (X/Al)
s a m p l e
/(X/Al)
c r u s t
(1)
As e x p e c t e d , B, S, V, Zn, As, Se, Sb, and the halogens were found t o be s t r o n g l y e n r i c h e d . The elements of i n t e r e s t i n t h i s study, B, S, and Se have EF v a l u e s of 35±22, 910±420, and 1940±980, r e s p e c t i v e l y . P r e l i m i n a r y r e s u l t s show the lowest B ( g ) , S O 2 , S e ( p ) , and s u l f a t e c o n c e n t r a t i o n s d u r i n g IS t o Ε winds and the h i g h e s t v a l u e s d u r i n g SW to NW winds. A summary of the d a t a i s shown i n F i g u r e 4, and p e r i o d s a p p a r e n t l y a f f e c t e d by c o a l - d e r i v e d a e r o s o l are c l e a r l y seen. A s e r i e s of e x p e r i m e n t s were conducted w i t h a c t i v a t e d - c h a r c o a l impregnated f i l t e r s b e i n g used i n both s i d e - b y - s i d e s t u d i e s and i n
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.
Tracing Emissions from Coal-Fired Power Plants
KITTO AND ANDERSON
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Filter Cassettes
Rubber Gaskets
h
Ί 12.3 cm
F i g u r e 1. Schematic of s t a c k e d - f i l t e r sampler used f o r s i m u l t a n e o u s c o l l e c t i o n of p a r t i c l e s and a c i d i c g a s e s .
Particles and gas phase ~.
Η Li
Be
Na
Mg
•
- " N U yuo r.uo^
lllllllll lllllllll κ Ca Sc Ti Y Cr Mn Fe Co lllllllll • 1 1 llllllll llllllll lllllllll • 1 1 llllllll llllllll • 1 Rb Sr Y Zr Nb Mo Tc Ru Rh • Cs 1 1 lllllllll llllllll • w1 1 Re Os Ir Da La Hf Ta lllllllll lllllllll llllllll llllllll lllllllll lllllllll llllllll Fr Ra Ac Ce
llllllll Th llllllll
Pr
Nd
Pa
lllllllll υ 111
He
K
Particles
Pm Sm Np
Eu
Gd
Ni Pd Pt
1
c
Al
Si
llllllll lllllllll Ga Ge llllllll llllllll llllllll Ag Cd In Sn llllllll llllllll llllllll Au Hg Tl Pb llllllll llllllll Cu
Tb Dy
llllllll llllllll llllllll lllllllll Pu Am Cm Bk
Β
Cf
Zn
Ho Es
Er Fm
Tm Md
Ν
0
F
Ne
Ρ
S
Cl
Ar
As
Se
Br
Kr
Sb
Te
1
Xe
^ ?
Bi
Po
Yb
Lu
At
Rn
llllllll llllllll No Lr
F i g u r e 2. A t m o s p h e r i c p a r t i c u l a t e and gas-phase elements, o b s e r v e d w i t h INAA, PGAA and IC, c o l l e c t e d by the s t a c k e d - f i l t < method.
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.
THE CHEMISTRY OF ACID RAIN
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Stacked
Stage 1 Particle
ZZl s/100
Stage 2 }
Filter
Stage 3
Stage 4
Gas Phase
(S3 Β
ci/10
\
ESS3 Br
Kg ι
F i g u r e 3. S t a g e - b y - s t a g e a t m o s p h e r i c p a r t i c u l a t e and gas-phase c o n c e n t r a t i o n s of t y p i c a l C o l l e g e Park, MD sample.
College
P a r k , MD
May - July. 1984
F i g u r e 4. V a r i a t i o n s of a t m o s p h e r i c c o n c e n t r a t i o n s of t r a c e elements i n the gas and p a r t i c u l a t e phase observed d u r i n g a c o n t i n u o u s two-month sampling p e r i o d .
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.
7.
KITTO AND ANDERSON
Tracing Emissions from Coal-Fired Power Plants
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/
s e r i e s with L i O H - t r e a t e d f i l t e r s . The r e s u l t s i n d i c a t d t h a t the gaseous s p e c i e s c o n t a i n i n g B, S and As were e f f i c i e n t l y t r a p p e d by the b a s e - t r e a t e d f i l t e r s , as none was observed above b l a n k l e v e l s on the c h a r c o a l f i l t e r s when used i n s e r i e s b e h i n d the b a s e - t r e a t e d filters. A p p r o x i m a t e l y e q u a l amounts of a c i d i c and n o n a c i d i c ( i . e . , o r g a n i c ) C I , B r , and I were o b s e r v e d , w h i l e about twice as much Se was found t o be a c i d i c . I n c o n c l u s i v e e v i d e n c e e x i s t f o r Sb, as t h i s element was observed o n l y once on each f i l t e r type d u r i n g the s a m p l i n g p e r i o d . R e s u l t s f o r Hg i n d i c a t e t h a t o n l y about 4% of the gaseous form of t h i s element i s trapped by the b a s e - t r e a t e d f i l t e r s , assuming no l o s s d u r i n g i r r a d i a t i o n , and the gas-phase i s dominated by n o n a c i d i c s p e c i e s . In agreement w i t h Germani ( 1 2 ) , c h a r c o a l f i l t e r s a p p a r e n t l y r e t a i n Hg d u r i n g n e u t r o n i r r a d i a t i o n . The c o n c l u s i o n from these experiments i s t h a t o r g a n i c ( e . g . , G ^ B r ) and e l e m e n t a l ( e . g . , S e ° ) s p e c i e s i n the atmosphere a r e not c o m p l e t e l y t r a p p e d by the ' L i O H - t r e a t e d f i l t e r s . Charcoal-impregnated filters a r e not r o u t i n e l y used due t o the s i g n i f i c a n t l y h i g h e r blank l e v e l s than the b a s e - t r e a t e d f i l t e r s (10, 30, 15, 2, 2, and 10 times h i g h e r f o r B, C l , As, Se, B r , and Sb, r e s p e c t i v e l y ) , the s p e c t r a l i n t e r f e r e n c e from the h i g h amount of Mn p r e s e n t and the i n a b i l i t y to a n a l y z e the f i l t e r m a t r i x by IC. A comparison of observed p a r t i c u l a t e c o n c e n t r a t i o n s from t h i s s t u d y t o one conducted about e i g h t y e a r s ago at the same s i t e (13) showed no measureable change f o r a l l the elements a s s o c i a t e d w i t h a c r u s t a l component, w i t h A l and L a b e i n g r e p r e s e n t a t i v e ( T a b l e I ) . Other elements ( e . g . , S, Se) which showed enrichments i n the e a r l i e r s t u d y c o n t i n u e d to be e n r i c h e d , but n o t a b l e d i f f e r e n c e s i n e l e m e n t a l c o n c e n t r a t i o n s e x i s t e d f o r V and Br, p r o b a b l y from d e c r e a s e d o i l and l e a d e d g a s o l i n e consumption ( 1 ) , r e s p e c t i v e l y . I t s h o u l d be noted t h a t d i s c r e p a n c i e s between the two s t u d i e s c o n c e n t r a t i o n s maybe due to s l i g h t v a r i a t i o n s i n sampling times (May-July vs Aug.-Sept.), methods ( T e f l o n vs Nuclepore f i l t e r s ) and meteorology, though these a r e thought to be minor. While most of the elements have n e a r l y i d e n t i c a l c o n c e n t r a t i o n s between the two s t u d i e s , and V and Br r a r e l y r e a c h e d the average l e v e l s of the p r e v i o u s s t u d y . 1
Table
I.
Typical Crustal
T y p i c a l Enriched
Notably
3
Comparison of Some E l e m e n t a l C o n c e n t r a t i o n s (ng/m ) Observed a t the C o l l e g e Park, MD S i t e w i t h Those Reported i n Aug.-Sept., 1976 f o r the Same S i t e (13)
Different
Elements:
Elements:
Elements:
T h i s Study (ri = 14) (1984)
Ko waleζyk (n = 20) (1976)
Al La
1200 ± 610 1.3 ± 0.8
1250 ± 620 1.4 ± 0.9
S Se
3700 ± 1800 2.3 ± 1.0
3100 ± 500 2.3 ± 1.3
V Br
10 ± 6 37 ± 17
20 ± 21 150 ± 100
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.
89
90
THE CHEMISTRY OF ACID RAIN
Application
of Data t o Receptor Modeling
U s i n g both a h y b r i d r e c e p t o r model, developed by Lewis and Stevens (2) and m o d i f i e d by Gordon and Olmez ( 3 ) , and a simple model of e m i s s i o n from the Ohio R i v e r V a l l e y , we compare t h e r e s u l t s of the C o l l e g e Park (CP) samples as w e l l as those of another c o n t i n u o u s set of samples taken from J u l y 3-29, 1983 a t Wallops I s l a n d , VA (WI), to p r e d i c t e d r e s u l t s . S i n g l e - s o u r c e d i f f e r e n t i a l e q u a t i o n s (2) are used t o d e s c r i b e the t i m e - v a r y i n g c o n c e n t r a t i o n s of S U 2 , S 0 4 and a p a r t i c u l a t e element c h a r a c t e r i s t i c of c o a l - f i r e d power p l a n t e m i s s i o n s (chosen here as S e ) . An a d d i t i o n a l e q u a t i o n (3) can be added to d e s c r i b e t h e c o n c e n t r a t i o n v a r i a t i o n of Β(0Η)3· The f o l l o w i n g r a t e c o n s t a n t s a p p l y t o the c o n c e n t r a t i o n s of the f o u r species i n question: k(t): d i s p e r s i o n and d e p o s i t i o n (a r a t e assumed t o be i d e n t i c a l f o r a l l four species) k ( t ) : pseudo f i r s t - o r d e r S O 2 c o n v e r s i o n r a t e ( f o r t h e e q u a t i o n s d e s c r i b i n g S O 2 and S0^~ c o n c e n t r a t i o n s ) and k ( t ) : a d d i t i o n a l d e p o s i t i o n l o s s r a t e f o r the gases ( S U 2 and B(0R) ). These two gaseous s p e c i e s a r e both a c i d i c and the wet and d r y d e p o s i t i o n c h a r a c t e r i c s a r e assumed to be s i m i l a r , y e t B(0H)3 does not undergo c o n v e r s i o n t o another s p e c i e s , t h e r e f o r e the S U 2 c o n v e r s i o n can be m o n i t o r e d by u s i n g gas-phase Β as a t r a c e r . In a s i m i l a r f a s h i o n , p a r t i c u l a t e Se i s assumed t o mimic s u l f a t e and can be used as a t r a c e r of S ( J - t o - s u l f a t e c o n v e r s i o n . The s o l u t i o n s t o the e q u a t i o n s f o r t h e f o u r s p e c i e s are as f o l l o w s :
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=
r
d
3
2
M
s o 2
M M
B
Se
M
= M
s o 2
(0)C(0)exp[-(k +k )t] r
(2)
d
= M (0)C(0)exp[-7 t] B
β
S 0 4
(3)
d
M (0)exp[-kt]
(4)
S e
=(3/2)M
s o 2
(0)C(U)[k /(k +k )][l-exp(-(k +k )t)] + M (0)C(0) r
r
d
r
d
S 0 4
(5)
where C(0) = M /M (0) k = (1/t)/ k d t k = (1/t)/ k dt' and k = (1/t)/ k dt . For our c a l c u l a t i o n s , we assume t h a t twenty i d e n t i c a l power-plants a r e spaced 50 km a p a r t over 1000 km, as a simple s i m u l a t i o n of the Ohio R i v e r V a l l e y r e g i o n , and t h a t c o a l - f i r e d power p l a n t s a r e t h e p r i m a r y s o u r c e of a t m o s p h e r i c B, S, and Se i n c o n t i n e n t a l r e g i o n s . U s i n g the most r e l i a b l e d a t a a v a i l a b l e from the l i t e r a t u r e about B ( g ) , S O 2 , and Se(p) r e l e a s e ( 3 ) , and assuming a t m o s p h e r i c m i x i n g t o 1.5 km, an average wind v e l o c i t y of 10 km/hr, a f i n e p a r t i c u l a t e (Se and s u l f a t e ) d e p o s i t i o n v e l o c i t y of 0.5 cm/s, a gas phase (B and S 0 ) d e p o s i t i o n v e l o c i t y of 2 cm/s, and a S 0 c o n v e r s i o n r a t e of 1.0%/hr, we can p r e d i c t t h e a t m o s p h e r i c c o n c e n t r a t i o n s and t h e i r r a t i o s as a f u n c t i o n of d i s t a n c e (Table I I ) . F l u c t u a t i o n s i n the model parameters w i l l s l i g h t l y cnange the p r e d i c t e d v a l u e s , and s h i f t the model p l o t s as a whole. The r a t i o v a l u e s r e p o r t e d f o r the s i t e s r e p r e s e n t the means of the i n d i v i d u a l sample r a t i o s . The model i n p u t s
S e
f
d
d
f
r
2
r
2
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.
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7.
KITTO AND
Tracing EmissionsfromCoal-Fired Power Plants
ANDERSON
parameters used were o n l y a " f i r s t t r y " but c o n c e n t r a t i o n s observed at C o l l e g e Park agree r e a s o n a b l y w e l l f o r such a s i m p l e model. We a r e i n the p r o c e s s of a t t e m p t i n g a more r e a l i s t i c r e p r e s e n t a t i o n of the Ohio R i v e r V a l l e y based on a c t u a l power p l a n t l o c a t i o n s and o u t p u t s . The model was d e s i g n e d to p r e d i c t r a t i o s , y e t the i n d i v i d u a l c o n c e n t r a t i o n s a l s o agree q u i t e w e l l . For the Wallops I s l a n d s t u d y , the observed gas-phase Β c o n c e n t r a t i o n s are e x c e p t i o n a l l y l a r g e , but t h i s i s not s u r p r i s i n g as l a r g e c o n c e n t r a t i o n s of gaseous B(0H)3 have been p r e v i o u s l y r e p o r t e d at marine s i t e s ( 8 ) . A d d i t i o n a l ambient measurements, i d e n t i f i c a t i o n of o t h e r s o u r c e s of gas-phase Β ( i f a n y ) , accompaning r a i n a n a l y s i s , and a more r i g o r o u s d e f i n i t i o n of i n p u t parameters w i l l h e l p r e f i n e the model. A l s o , comparing sample-to-sample v a r i a t i o n s w i t h wind b a c k - t r a j e c t o r y i n f o r m a t i o n may h e l p determine i f such a model can be a p p l i e d to l a r g e d i s t a n c e s c a l e s (~1500 km or more).
Table
II.
Comparison of H y b r i d Receptor Model w i t h Observed C o n c e n t r a t i o n s at C o l l e g e Park, MD (CP) and Wallops I s . , VA (WI) Concentration Predicted at D i s t a n c e (km)
species
Observed CP (May-July, 1984)
Observed WI (July, 1983)
100
700
1000
1800
14 samples
12
samples
16 12
27 22
28 23
0.2 0.53
14.0 15.7
±5.1 ± 6.5
8.1 ± 70 ±
1.0 0.7
14 2.5
19 3.0
11 1.0
11.2 2.3
± 5.4 ± 1.0
0.04 0.75 570
0.35 0.81 1900
0.46 0.82 2100
26.0 1.80 3100
gases
S0 Β
3
2
(yg/m ) (ng/m ) 3
4.9 50
particles
S0 Se
3
4
(yg/m ) (ng/m ) 3
13.2 1.76
± ±
7.5 0.91
ratios
S(p)/S(g) B ( g ) / S 0 xlOOO S(p)/Se(p) 2
0.56 1.11 1710
i 0.24 ± 0.25 ± 530
1.20 ± 0.38 7.9 ± 2.7 770 3040
Literature Cited 1.
Kowalczyk, G. S.; Choquette, C. E.; Gordon, G. E. Atmos. Environ. 1978, 12, 1143. 2. Lewis, C. W.; Stevens, R. K. Atmos. Environ. 1985, 19, 917. 3. Gordon, G. E.; Olmez, I. APCA Specialty Conference on Receptor Methods for Source Apportionment: Real World Issues and Applications, Williamsburg, VA, 1985.
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.
91
THE CHEMISTRY OF ACID RAIN
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92
4. Gladney, E.S.; Wangen, L. E.; Curtis, D. B.; Jurney, Ε. T. Environ. Sci. Technol. 1978, 12, 1084. 5. Egarov, A. P.; Laktionova, Ν. V.; Popinako, Ν. V.; Novoselova, I. V. Therm. Engin. 1979, 26, 82. 6. Kitto, M. E.; Anderson, D. L.; Gordon, G. E.; Ondov, J. M. 186th National ACS Meeting, Washington, D.C., 1983. 7. Fogg, T. R.; Rahn, K. A. Geophys. Res. Let. 1984 1, 854. 8. Fogg, T. R. Ph.D. Thesis, University of Rhode Island, Kingston, 1983. 9. Failey, M. P.; Anderson, D. L.; Zoller, W. H.; Gordon G. E.; Lindstrom, R. M. Anal. Chem. 1979, 51, 2209. 10. Germani, M. S.; Gokmen, I.; Sigleo, A. C.; Kowalczyk, G. S.; Olmez, I.; Small, A. M.; Anderson, D. L.; Failey, M. P.; Gulovali, M. C.; Choquette, C. E.; Lepel, Ε. Α.; Gordon, G. E.; Zoller, W. H. Anal. Chem. 1980, 52, 240. 11. Wedepohl, Κ. H. In Origin and Distribution of the Elements, Ahrens, L. H., Ed.; Pergamon Press: London, 1968; p 999. 12. Germani, M. S. Ph.D. Thesis, University of Maryland, College Park, 1980. 13. Kowalczyk, G. S. Ph.D. Thesis, University of Maryland, College Park, 1979. From a dissertation to be submitted to the Graduate School, University of Maryland, by Michael E. Kitto in partial fulfillment of the requirements for the Ph. D. degree in Chemistry. Although the research described in this article has been funded wholly or in part by the United States Environmental Protection Agency under assistance agreement R-812503-01-0 to the University of Maryland, it has not been subjected to the Agency's peer and administrative review and therefore may not necessarily reflect the views of the Agency and no official endorsement should be inferred. RECEIVED
March 10, 1987
Johnson et al.; The Chemistry of Acid Rain ACS Symposium Series; American Chemical Society: Washington, DC, 1987.