Major, Minor, and Trace Element Composition of Coal and Fly Ash, as

Jul 22, 2009 - This multi-element capability makes possible the detailed chemical analysis of coal and combustion products. A comparison to National B...
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10 Major, Minor, and Trace Element Composition of Coal and Fly Ash, as

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Determined by Instrumental Neutron Activation Analysis Κ. H. ABEL and L. A. RANCITELLI Battelle, Pacific Northwest Laboratories, Richland, Wash. 99352 A highly sensitive instrumental neutron activation analysis (INAA) technique can determine 30-40 eléments in coal and fly ash including Sb, As, Se, Hg, Zn, and V which are elements of environmental concern. This multi-element capability makes possible the detailed chemical analysis of coal and combustion products. A comparison to National Bureau of Standards-Environmental Protection Agency fuel standards shows that a high degree of accuracy and precision is attainable, allowing tentative conclusions to be drawn as to the origin of certain elements in the coal and their fate during combustion.

' n p h e c u r r e n t emphasis o n t h e large-scale e x p l o i t a t i o n of c o a l as a c o m m e r c i a l e l e c t r i c a l e n e r g y source makes a m o r e t h o r o u g h u n d e r s t a n d i n g of t h e c h e m i s t r y of c o a l a n d t h e b y - p r o d u c t s of c o a l c o m b u s t i o n i n c r e a s i n g l y i m p o r t a n t . A n e x a m p l e of p l a n n e d large-scale c o a l use f o r p o w e r g e n e r a t i o n is t h e p r o p o s e d

N o r t h C e n t r a l P o w e r Project.

This

project

w i l l use t h e vast c o a l reserves i n t h e F o r t U n i o n F o r m a t i o n i n N o r t h Dakota, South Dakota, Montana, a n d W y o m i n g .

T h e c o a l resources i n

this area are e s t i m a t e d t o b e 4 0 % of t h e U . S . t o t a l reserves.

The North

C e n t r a l P o w e r S t u d y ( 1 ) estimates t h a t b y 1980 a steam-fired g e n e r a t i n g c a p a c i t y o f 53,000 M W w i l l exist i n a n area b e t w e e n C o l s t r i p , M o n t a n a , a n d G i l l e t t e , W y o m i n g . E a c h 1000 M W of p o w e r g e n e r a t e d w i l l r e q u i r e c o n s u m p t i o n o f a p p r o x i m a t e l y 4 m i l l i o n tons of c o a l / y r .

Thus, the total

coal consumption w i l l be approximately 210 m i l l i o n tons/yr. p u t this c o a l c o n s u m p t i o n i n p e r s p e c t i v e ,

T o help

the D e p a r t m e n t of I n t e r i o r

118 In Trace Elements in Fuel; Babu, S.; Advances in Chemistry; American Chemical Society: Washington, DC, 1975.

10.

ABEL AND RANCiTELLi

Instrumental

Neutron Activation

Analysis

119

e s t i m a t e d t h a t 326 m i l l i o n tons of c o a l w e r e u s e d for e l e c t r i c a l g e n e r a t i o n i n the e n t i r e U n i t e d States i n 1970 ( 2 ) .

T h e r e f o r e , the e s t i m a t e d 210

m i l l i o n tons represents a p p r o x i m a t e l y 6 5 % of the t o t a l u s e d f o r e l e c t r i c a l g e n e r a t i o n i n 1970. T o illustrate the possible i m p a c t of this t y p e of d e v e l o p m e n t , some f u r t h e r c a l c u l a t i o n s c a n be p e r f o r m e d u s i n g present e m i s s i o n standards and

r e p r e s e n t a t i v e c o a l concentrations.

s u l f u r c o n c e n t r a t i o n of 0 . 6 5 %

F i r s t , i f one uses a n

average

t y p i c a l of l o w s u l f u r w e s t e r n coals a n d

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assumes the e s t i m a t e d c o a l c o n s u m p t i o n , 2.7 m i l l i o n tons of s u l f u r d i o x i d e w i l l b e p r o d u c e d p e r year. T h e emphasis i n recent e n v i r o n m e n t a l i m p a c t studies of fossil f u e l p o w e r p l a n t s has b e e n o n s u l f u r d i o x i d e e m i s s i o n a n d associated a c i d rains w h i c h h a v e h a d d e t r i m e n t a l effects o n s u r r o u n d ing vegetation

(3,

4, 5 ) .

T h e r e are F e d e r a l standards to l i m i t s u l f u r

d i o x i d e emissions, a n d the t e c h n o l o g y for s u l f u r r e m o v a l r e q u i r e d to m e e t these standards is d e v e l o p i n g i n s e v e r a l a l t e r n a t i v e p a t h w a y s , a l l s t i l l i n e x p e r i m e n t a l stages. fications

T h u s , t h e r e u n d o u b t e d l y w i l l be n u m e r o u s m o d i -

a n d alterations i n p l a n t d e s i g n before s u l f u r d i o x i d e is r e m o v e d

o n a f u l l - t i m e a n d large-scale basis.

B u t e v e n u n d e r these standards,

e m i s s i o n of 2.1 m i l l i o n tons of s u l f u r d i o x i d e / y r w o u l d b e a l l o w e d , a s s u m i n g a c o a l c o n s u m p t i o n of 210 m i l l i o n tons. S e c o n d l y , i f it is a s s u m e d t h a t the c o a l has a n ash figure of

15%

u p o n c o m b u s t i o n ( w h i c h appears reasonable for these c o a l s ) a n d 9 9 % efficiency is a s s u m e d for the p r e c i p i t a t o r s , 315,000 tons of fly ash c o u l d b e released p e r y e a r u n d e r the p r o j e c t e d c o a l c o n s u m p t i o n . F i n a l l y , the trace constituents b e c o m e i m p o r t a n t factors w h e n s u b s t a n t i a l a m o u n t s of c o a l are b u r n e d . S e l e n i u m , w h i c h is present at a p p r o x i m a t e l y 2 p p m i n c o a l , c o u l d be released at a rate of 210 t o n s / y r , a s s u m i n g 210 m i l l i o n tons of c o a l c o n s u m e d a n d a 5 0 % escape rate d u r i n g c o m b u s t i o n (6).

S i g n i f i c a n t discharges c o u l d also b e e x p e c t e d for H g ,

F , A s , and perhaps Sb, Z n , a n d C u . T h u s i t becomes a p p a r e n t that, for the v e r y h i g h p r o j e c t e d

coal

c o n s u m p t i o n i n this r e g i o n , the d i s c h a r g e of trace constituents is i m p o r tant, a n d p o t e n t i a l e n v i r o n m e n t a l i n t e r a c t i o n a n d effects w a r r a n t i m m e diate attention.

T h e r e has b e e n some a t t e n t i o n g i v e n to

radioactive

elements i n c o a l a n d t h e i r release d u r i n g c o m b u s t i o n (7, 8,9).

However,

the stable e l e m e n t trace constituents are p e r m a n e n t p o l l u t a n t s of

the

e n v i r o n m e n t , a n d t h e i r i m m e d i a t e a n d p o t e n t i a l l o n g - t e r m effects s h o u l d be investigated. R e s e a r c h i n d i c a t e s t h a t a significant f r a c t i o n ( 5 0 - 9 0 % ) of m e r c u r y is v o l a t i l i z e d a n d lost d u r i n g c o a l c o m b u s t i o n (10, 11, 12)

a n d that m a n y

of the p o t e n t i a l l y h a z a r d o u s trace elements a p p e a r c o n c e n t r a t e d finer p a r t i c u l a t e emissions (13,

14).

upon

S e v e r a l investigators h a v e o b s e r v e d

e n r i c h m e n t of these h a z a r d o u s elements u p o n p a r t i c u l a t e s i n u r b a n areas

In Trace Elements in Fuel; Babu, S.; Advances in Chemistry; American Chemical Society: Washington, DC, 1975.

120

TRACE

(15-23),

i n remote

C a n a d a (25),

ELEMENTS

locations s u c h as A n t a r c t i c a (24)

a n d i n the u p p e r a t m o s p h e r e

IN

FUEL

and Northern

(26).

T h e r e are several factors w h i c h m a k e n e u t r o n a c t i v a t i o n analysis (NAA)

a n a p p r o p r i a t e t e c h n i q u e for i n v e s t i g a t i n g p o t e n t i a l p o l l u t a n t s

i n c o a l a n d the c o m b u s t i o n process.

F i r s t , the m u l t i - e l e m e n t n a t u r e of

N A A is u s e f u l because of the l a r g e n u m b e r of p o t e n t i a l e l e m e n t a l p o l ­ lutants, s u c h as Se, H g , A s , Z n , N i , S b , a n d C d . A l s o , the use of e l e m e n t a l ratios m a d e possible b y the m u l t i - e l e m e n t c a p a b i l i t y facilitates the u n d e r ­

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s t a n d i n g of c h e m i c a l b e h a v i o r d u r i n g the c o m b u s t i o n process. E l e m e n t a l ratios h a v e b e e n u s e d p r e v i o u s l y i n u r b a n ( 1 5 ) (26)

studies.

and upper atmospheric

S e c o n d l y , the s e n s i t i v i t y a n d s e l e c t i v i t y of N A A a l l o w s

d e t e r m i n a t i o n of m a n y elements present at v e r y l o w concentrations ( p p m or l o w e r ) , a n d the results are unaffected b y m a t r i x interferences.

This

s e n s i t i v i t y also a l l o w s analysis of v e r y s m a l l samples. F i n a l l y , t h e cost of N A A w h e n c o n d u c t e d as a m u l t i - e l e m e n t a n a l y t i c a l t o o l is c o m p e t i t i v e w i t h m o r e c o n v e n t i o n a l a n d less sensitive t e c h n i q u e s o n the

cost-per-

e l e m e n t - p e r - s a m p l e basis. Battelle (INAA)

has

developed

instrumental neutron

a c t i v a t i o n analysis

t e c h n i q u e s w h i c h p e r m i t v e r y sensitive a n d accurate

multi­

e l e m e n t analysis of a p p r o x i m a t e l y 40 elements i n c o a l a n d fly ash. T h e s e t e c h n i q u e s , w h i c h w i l l b e d e s c r i b e d i n this w o r k , f o r m the basis extensive e n v i r o n m e n t a l studies of the effluent f r o m c o a l - p o w e r e d

for gen­

e r a t i n g f a c i l i t i e s a n d other p o l l u t i o n sources. Experimental T h e s e t e c h n i q u e s are d e s i g n e d to m i n i m i z e b o t h the a c t u a l w o r k i n g t i m e , r e q u i r e d a n d the a n a l y t i c a l u n c e r t a i n t i e s i n s a m p l e analysis. S a m p l e p r e p a r a t i o n a n d n e u t r o n a c t i v a t i o n p r o c e d u r e s are b a s e d o n p r o v e d a n a ­ lytical and microanalytical techniques. reliability, and accuracy

T h e unusually h i g h sensitivity,

are a c h i e v e d t h r o u g h a c h o i c e of

optimum

i r r a d i a t i o n a n d c o u n t i n g times for the γ-ray d e t e c t i o n systems. Sample Preparation. T h e c o a l a n d fly ash samples are w e i g h e d i n t o s m a l l bags f o r m e d b y f o l d i n g a n d h e a t - s e a l i n g p o l y c a r b o n a t e

film.

The

openings are also heat-sealed after the samples are p l a c e d i n t o t h e p o l y ­ c a r b o n a t e bags.

T h e p o l y c a r b o n a t e film, s u p p l i e d b y N u c l e o p o r e , is the

stock m a t e r i a l u s e d for N u c l e o p o r e p o l y c a r b o n a t e filters a n d is d e s i r a b l e b e c a u s e of its l o w trace m e t a l content.

T h e heat s e a l i n g is a c c o m p l i s h e d

u s i n g a T e f l o n - c o a t e d " Q u i k S e a l " t h e r m a l i m p u l s e sealer m a n u f a c t u r e d b y N a t i o n a l I n s t r u m e n t C o . T h e p o l y c a r b o n a t e bags are t h e n p l a c e d i n t o a c l e a n p o l y e t h y l e n e v i a l ( a p p r o x i m a t e l y 2.5 c m l o n g X dram).

1.0 c m I D - 2 / 5

T h e v i a l c o n t a i n i n g the c o a l a n d fly ash samples is t h e n p l a c e d

i n t o a n o t h e r c l e a n v i a l (5.5 c m l o n g X

1.43 c m I D - 2 d r a m ) p r i o r to

neutron activation.

In Trace Elements in Fuel; Babu, S.; Advances in Chemistry; American Chemical Society: Washington, DC, 1975.

10.

ABEL AND RANCiTELLi

Table I.

Neutron

Activation

121

Analysis

Irradiation and Counting Procedures for Coal and Fly Ash

IRRADIATION INTERVAL/ DECAY NEUTRON FLUX* INTERVAL

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Instrumental

COUNT INTERVAL

INSTRUMENTATION

1,000-10,000 MIN

Nal σΐ) MULTI-DIMENSIONAL γ - R A Y SPECTROMETER

K, Th, U

(15-1 min/lxl(r 10 Ml Ν

5 MIN

Ge (Li)

Al, Br, CI, Cu, Mg, Mn, Na, Ti, V

6-8 hrs/5xl0 1 2

10 MIN

Ge (Li) OR ΑΝΤΙ-COINCIDENCE SHIELDED Ge (Li)

As, Au, Ba, Br, Ca, K, La, Lu, Na, Sm, Yb

4-7 DAYS

- 3 0 DAYS

ELEMENTS DETERMINED

Ag, Eu, Sb, Tb,

100-1,000 MIN

Ce, Co, Cr, Cs, Fe, Hf, Hg, Ni, Rb, Se, Se, Sr, Ta, Th, Zn

* NEUTRONS/CM2/SEC

S t a n d a r d s u s e d f o r comparators are either w e l l d o c u m e n t e d m a t e r i a l s ( U . S . G . S . B C R - 1 Basalt, N B S O r c h a r d Leaves, N B S Bovine L i v e r , etc.) or a r e p r e p a r e d i n t h e l a b o r a t o r y b y p i p e t t i n g k n o w n q u a n t i t i e s of ele­ ments onto h i g h p u r i t y cellulose m a t e r i a l . S t a n d a r d s a r e w e i g h e d

into

p o l y c a r b o n a t e a n d p a c k a g e d f o r i r r a d i a t i o n i n t h e same m a n n e r as t h e samples. Neutron Activation Analysis. T h e analysis consists o f t w o i r r a d i a ­ t i o n p e r i o d s a n d three c o u n t i n g intervals as s h o w n i n T a b l e I . G a m m a ray

spectrometry

is a c c o m p l i s h e d

b y state-of-the-art

Ge(Li)

diodes,

t y p i c a l l y w i t h 1 5 - 2 0 % efficiency r e l a t i v e to 3 X 3 " N a l ( T l ) detector a n d < 2 K e V r e s o l u t i o n ( f u l l w i d t h a t h a l f m a x i m u m ) at t h e 1332 K e V energy.

6 0

Co

T h e γ-ray spectra f r o m samples a n d standards a r e ' stored o n

m a g n e t i c tape a n d t h e d a t a r e d u c e d b y a P D P - 1 5 c o m p u t e r .

A computer

p r o g r a m (27) w a s d e v e l o p e d to i d e n t i f y t h e r a d i o n u c l i d e s present f r o m t h e i r c h a r a c t e r i s t i c γ-ray energies, c a l c u l a t e n e t peak areas, a n d c o n v e r t net p e a k areas to element w e i g h t s b y d i r e c t c o m p a r i s o n to k n o w n s t a n d ­ ards, thus c a l c u l a t i n g t h e c o n c e n t r a t i o n of t h e elements i n t h e o r i g i n a l samples. T a b l e I I s u m m a r i z e s the parameters w h i c h relate to t h e m e a s u r e m e n t of e a c h element: n e u t r o n a c t i v a t i o n p r o d u c t s , h a l f - l i v e s , γ-ray energies, lengths of i r r a d i a t i o n , d e c a y , a n d c o u n t i n g . A l s o l i s t e d are t h e possible i n t e r f e r i n g r a d i o n u c l i d e s a n d i n t e r f e r i n g reactions p r o d u c i n g t h e same isotopes f r o m another element w h i c h w e r e necessarily e v a l u a t e d . t a b l e is s u b d i v i d e d i n t o three sections r e p r e s e n t i n g t h e elements

This deter­

m i n e d d u r i n g e a c h o f t h e three c o u n t i n g i n t e r v a l s . T h e i n t e r f e r i n g reactions w e r e e v a l u a t e d b y i r r a d i a t i o n of p u r e ele­ m e n t standards w i t h corrections

applied where

necessary.

T h e only

In Trace Elements in Fuel; Babu, S.; Advances in Chemistry; American Chemical Society: Washington, DC, 1975.

122

TRACE ELEMENTS

Table I I - A .

I N FUEL

Nuclear D a t a Relating to the Measurement of the Elements in Coal and Fly A s h INTERVAL-0.5-1.0 Ml Ν C - 1x1013 NEUTRONS/cm2/sec

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ELEMENT

TARGET ISOTOPE

ISOTOPIC ABUNDANCE

< % )

PRODUCT NUCLIDE

HALFLIFE

THERMAL NEUTRON CROSS SECTION

A.

2.31m

0.24

Br

17.6m

8.5

BEST y FOR MEASUREMENT (KEV)

NUMBER OFy's PER 1000 DECAYS

1779

1000

NONE

ul

617

70

666(10)

108

1643

380

2170(470)

NONE

1039

90

NONE

70

b

Al

27

AI

100

B

Br

7

V

50.5

80

CI

37

CI

24.5

*CI

37.3m

b 0.4 b

Cu

65

Cu

30.9

«Cu

5.10m

2.3

POSSIBLE INTERFERING NUCLIDE IN DIODE MEASUREMENT

ASSOCIATED y-RAYS KEV (yls/1000 DISINTEG)

POSSIBLE INTERFERING NUCLEAR REACTIONS PRODUCING NUCLIDES OF INTEREST

^Siln.pA

Nd(1776) Ag(614)

31

Ρ(η,α)

80

Kr(n.p» 8 0 Br

*ΑΓ(η.ρ)3ΐ Κ(η,α) « C l

b

Ga(1040)

71

Zn(1040) 69

Mg

Mn

Na

Ti

Mg

26

55

Mn

Na

23

50

Ti

11.2

27

100

9.45m

Mg

^Mn

100

24

5.3

Na

51

0.027 b

2.58h

13.3

0.53

15.0Π

Ti

5.79m

0.14

844

700

1014

300

847

990

1811

290

b

1369

1000

b

320

b

M(X840) u l Nd(84D 87 Kr(846) 56ΜΠ(847)

180(70)

101

ÏJÎMol 1012) tat 1016) ^ S n d O l T ) 188ReU018) 15

2110(150)

27

Mg(844)

2754(1000)

950

v

51

99.8

52

Table II-B.

V

3.76m

4.9

b

1434

As

TARGET ISOTOPE

75

AS

ISOTOPIC ABUNDANCE

(%> 100

117

Cd(1373

Z7

Au

100

p^Mn

,Mg(n,p)24Na AI(n,a) 2 4 N a

1

NONE

Ru(317)

1 3 9

BZm

Ta(318)

^Crln.a)

51

Ti

{W*V

Ba( 1430)

Mn(n,a) V 52

Nuclear Data Relating to the Measurement of the Elements in Coal and Fly A s h

PRODUCT HALFNUCLIDE LIFE

76

As

26.5h

THERMAL NEUTRON BEST r FOR CROSS MEASUREMENT (KEV) SECTION

4.5 b

559

j

NUMBER OF r s PER 1000 DECAYS

430

ASSOCIATED Τ-RAYS KEV

POSSIBLE INTERFERING NUCLIDE IN DIODE MEASUREMENT

(Y's/1000DISINTEG) 1220(50) 1440(7)

0s(558)

193

114m

POSSIBLE INTERFERING NUCLEAR REACTIONS PRODUCING NUCLIDES OF INTEREST

ln(558) 82Br1554)

As(562) 122Sb(564)

Au

Mg

JJ?Pt(317) f_V

160

14(

la(398)

67

79

Nd(398) 233PaG98>

147

75se(401)

In Trace Elements in Fuel; Babu, S.; Advances in Chemistry; American Chemical Society: Washington, DC, 1975.

24

Na

Eu(n.p.

153

Sm

Gd(n,a)

153

Sm

153

182

156

Yb

42

Ce«n.p» 1 4 0 La

Eu(1596)

177m Lu(2M ) 199Au(2fjg) Na

Ca(n.p. 4 2 K

Sc(n.a)

NONE

10.

Instrumental

A B E L AND RANCITELLI

Table II-C.

Neutron Activation

123

Analysis

Nuclear Data Relating to the Measurement of the Elements in Coal and Fly Ash IRRADIATION PARAMETERS j

ISOTOPIC ABUNDANCE (%)

TARGET ISOTOPE

ELEMENT

48.65

Ag

PRODUCT HALFNUCLIDE LIFE

110m

Ag

THERMAL NEUTRON CROSS SECTION

3b

255(1

BEST Τ FOR MEASUREMENT (KEV)

658

NUMBER OFY's PER 1000 DECAYS

960

680(160) 706(190)

POSSIBLE INTERFERING NUCLEAR REACTIONS PRODUCING NUCLIDES OF INTER

POSSIBLE INTERFERING NUCLIDE IN DIODE MEASUREMENT

ASSOCIATED 7 -RAYS KEV (Y's/IOOODISINTEG)

Eu

1 1 (

152

764(230) 818(80)

113

Wp»

1 1 0

ln(n.a.

%

U

° %

140

Ce

885(710) 937(320) 1384(210) 1505(110) Ce

140

Ce

88.48

141

Ce

32.5d

0.6 b

145

480

NONE

Pa(145) 127Xe(145)

Fe(142)

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59

177m

Co

59

Cr

100

Co

4.31

Cr

50

60

51

Co

Cr

5.24y

27.8d

37 b

17 b

1173

1000

1332

1000

320

90

NONE

Lu