8 Currently Available Geophysical Methods for Use in Hazardous Waste Site Investigations ROY B. EVANS
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U.S. Environmental Protection Agency, Environmental Monitoring Systems Laboratory, Las Vegas, NV 89114 Monitoring to estimate exposure is e s s e n t i a l to risk assessment near sources of exposure. Cost- e f f e c t i v e hazardous waste s i t e assessments i n c l u d e three phases: (1) p r e l i m i n a r y site assessment, utilizing aerial photography and site i n s p e c t i o n s ; (2) geophysical surveys to p i n p o i n t buried wastes and to help define plumes of conductive contaminants in groundwater; and (3) c o n f i r m a t i o n of groundwater contamination through monitoring w e l l networks designed on the b a s i s of the geo p h y s i c a l survey. C u r r e n t l y a v a i l a b l e g e o p h y s i c a l methods most a p p l i c a b l e in hazardous waste site investigations i n c l u d e metal detectors and magnetometers ( u s e f u l in l o c a t i n g buried wastes); groundpenetrating radar ( u s e f u l in d e f i n i n g trench boundaries); electromagnetic i n d u c t i o n or EM (useful in surveys of shallow plumes of conductive groundwater contaminants); resistivity (useful i n surveys of site s t r a t i g r a p h y and deep groundwater contaminant plumes); and seismic methods (most u s e f u l in surveying geologic s t r a t i g r a p h y ) . M o n i t o r i n g i s u s u a l l y an e s s e n t i a l p a r t of r i s k assessment; e n v i r o n m e n t a l samples a r e c o l l e c t e d i n v a r i o u s media n e a r s o u r c e s o f p o t e n t i a l e x p o s u r e , and t h e s e s a m p l e s a r e a n a l y z e d f o r t o x i c substances suspected of being present. In the past, i n v e s t i g a t i o n o f h a z a r d o u s waste s i t e s h a s commonly depended upon d r i l l i n g t o o b t a i n i n f o r m a t i o n o n t h e g e o l o g i c s e t t i n g , upon m o n i t o r i n g w e l l s f o r s a m p l e s o f g r o u n d w a t e r , and upon l a b o r a t o r y a n a l y s i s o f s o i l and w a s t e s a m p l e s . D u r i n g t h e p a s t d e c a d e , e x t e n s i v e d e v e l o p m e n t i n remote s e n s i n g g e o p h y s i c a l e q u i p m e n t , f i e l d methods, a n a l y t i c a l t e c h n i q u e s , and a s s o c i a t e d computer p r o c e s s i n g h a s g r e a t l y i m p r o v e d o u r a b i l i t y t o c h a r a c t e r i z e hazardous waste s i t e s . Some g e o p h y s i c a l methods o f f e r a d i r e c t means o f d e t e c t i n g c o n t a m i n a n t p l u m e s , f l o w 0097-6156/82/0204-0093$06.25/0 © 1982 American Chemical Society
Long and Schweitzer; Risk Assessment at Hazardous Waste Sites ACS Symposium Series; American Chemical Society: Washington, DC, 1982.
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d i r e c t i o n , and b u r i e d drums. Some a r e a p p l i c a b l e t o measurements o f c o n t a m i n a n t s and d i r e c t i o n o f f l o w w i t h i n t h e v a d o s e z o n e ; o t h e r s o f f e r a way t o o b t a i n d e t a i l e d i n f o r m a t i o n a b o u t s u b s u r f a c e g e o l o g y . The c a p a b i l i t y t o c h a r a c t e r i z e t h e subsurface r a p i d l y without d i s t u r b i n g the s i t e o f f e r s b e n e f i t s i n t e r m s o f l e s s c o s t , l e s s r i s k , and b e t t e r u n d e r s t a n d i n g o f site conditions. C o s t - e f f e c t i v e d e s i g n o f h a z a r d o u s waste s i t e g r o u n d w a t e r i n v e s t i g a t i o n s i n v o l v e s an i n t e g r a t e d , t h r e e - p h a s e d a p p r o a c h : (1) p r e l i m i n a r y s i t e assessment, i n v o l v i n g t h e use o f a e r i a l p h o t o g r a p h y , o n - s i t e i n s p e c t i o n s , and r e a d i l y a v a i l a b l e i n f o r m a t i o n t o a p p r o x i m a t e s i t e b o u n d a r i e s and l o c a t i o n s o f w a s t e c o n c e n t r a t i o n s , a s w e l l as p r o b a b l e s i t e g e o l o g y ; ( 2 ) g e o p h y s i c a l s u r v e y s t o p i n p o i n t b u r i e d w a s t e s and e s t i m a t e q u a n t i t i e s , and t o d e l i n e a t e plumes o f c o n d u c t i v e c o n t a m i n a n t s i n g r o u n d w a t e r ; and ( 3 ) c o n f i r m a t i o n o f g r o u n d w a t e r c o n t a m i n a t i o n t h r o u g h m o n i t o r i n g w e l l n e t w o r k s d e s i g n e d on t h e b a s i s o f plumes and s u b s u r f a c e s t r a t i g r a p h y d e f i n e d by t h e geophysical surveys. The s p a t i a l c h a r a c t e r i z a t i o n o f t h e s i t e by g e o p h y s i c a l means c a n make p o s s i b l e t h e e f f i c i e n t l o c a t i o n o f m o n i t o r i n g w e l l s and t h e r e d u c t i o n o f r i s k s i n v o l v e d i n exploratory d r i l l i n g . Field
Problems
The t h r e e g e n e r a l o b j e c t i v e s u s u a l l y i n v o l v e d i n s u b s u r f a c e investigations are: • Location of buried m a t e r i a l s , • D e t e r m i n a t i o n o f t h e p r e s e n c e o f plumes and t h e d i r e c t i o n , r a t e o f movement, and d i s t r i b u t i o n o f contaminants; • C h a r a c t e r i z a t i o n of the geohydrologic conditions, n a t u r a l and manmade. L o c a t i o n o f b u r i e d m a t e r i a l s a t a hazardous waste s i t e i s u s u a l l y f o r the purpose of r e m e d i a l a c t i o n ; i . e . , e x c a v a t i n g t h e s e m a t e r i a l s and u l t i m a t e l y d i s p o s i n g o f them. The k e y unknowns a r e t y p e ( b u l k - d u m p e d o r p a c k a g e d i n drums o r o t h e r c o n t a i n e r s ) , q u a n t i t y (volume o f w a s t e ; number o f d r u m s ) , and l o c a t i o n , p a r t i c u l a r l y depth of b u r i a l . The c o n c e r n s a r e f o r s a f e e x c a v a t i o n w i t h o u t p u n c t u r i n g c o n t a i n e r s o r b r e a c h i n g any e x i s t i n g t r e n c h l i n e r s and t h u s a g g r a v a t i n g t h e c l e a n u p problems. D e t e r m i n a t i o n o f t h e p r e s e n c e o f c o n t a m i n a n t plumes and t h e i r f l o w d i r e c t i o n and movement r a t e i s commonly r e q u i r e d a t hazardous waste s i t e s . The f i r s t d e t e r m i n a t i o n i s w h e t h e r l e a k a g e from t h e hazardous waste s i t e i s o c c u r r i n g . I f the e x i s t e n c e o f a plume i s c o n f i r m e d , i t s d i r e c t i o n and e x t e n t s h o u l d be e s t a b l i s h e d and i d e n t i f i e d . A preliminary geophysical s u r v e y c a n a i d i n b e t t e r d e f i n i n g t h e c o n t a m i n a n t plume, l e a d i n g t o more e f f e c t i v e m o n i t o r i n g w i t h a s m a l l e r number o f m o n i t o r i n g wells.
Long and Schweitzer; Risk Assessment at Hazardous Waste Sites ACS Symposium Series; American Chemical Society: Washington, DC, 1982.
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C h a r a c t e r i z a t i o n o f the n a t u r a l s e t t i n g i s u s u a l l y a major p o r t i o n o f the f i e l d i n v e s t i g a t i o n . A t most s i t e s , p e r m e a b i l i t y o f t h e l o c a l s o i l and r o c k t y p e s , t h e d e p t h o f t h e w a t e r t a b l e , and t h e d i r e c t i o n o f g r o u n d w a t e r f l o w w i l l s t r o n g l y i n f l u e n c e movement o f c o n t a m i n a n t s f r o m t h e p o i n t o f d i s p o s a l . The anomalies which occur n a t u r a l l y w i t h i n the g e o h y d r o l o g i c s e c t i o n must be t a k e n i n t o c o n s i d e r a t i o n . S u r f a c e d r a i n a g e , sewers, and b u r i e d u t i l i t i e s c a n a f f e c t s u r f a c e and g r o u n d w a t e r f l o w a r o u n d a hazardous waste s i t e . Many o f t h e s e p r o b l e m s c a n o f t e n be a v o i d e d by t h e u s e o f an i n t e g r a t e d a p p r o a c h c o m b i n i n g c o n t e m p o r a r y g e o p h y s i c a l methods t o s u p p o r t t r a d i t i o n a l d r i l l i n g p r o c e d u r e s .
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Available Geophysical
Methodology
T h i s paper d i s c u s s e s s i x c u r r e n t l y a v a i l a b l e g e o p h y s i c a l s e n s i n g methods: g r o u n d p e n e t r a t i n g r a d a r ( G P R ) , e l e c t r o m a g n e t i c i n d u c t i o n (EM), r e s i s t i v i t y , s e i s m i c r e f r a c t i o n , m e t a l d e t e c t i o n , and m a g n e t o m e t r y . O t h e r g e o p h y s i c a l methods a r e a v a i l a b l e and a r e p r o v i n g t o be e f f e c t i v e ; s t i l l o t h e r s ( f o r example, complex r e s i s t i v i t y ) a r e emerging. However, t h i s d i s c u s s i o n has been l i m i t e d t o t h e s i x methods i n v o l v e d i n t h e l a r g e s t number o f a c t u a l s i t e i n v e s t i g a t i o n s t o d a t e . T a b l e I shows t h e p o s s i b l e r o l e s o f e a c h o f t h e s e methods i n h a z a r d o u s waste s i t e assessments. These methods s h o u l d be r e g a r d e d a s c o m p l e m e n t i n g one a n o t h e r . No one method i s u s e d f o r a l l a p p l i c a t i o n s , a n d some methods a r e u s e f u l i n more t h a n one application. I n g e n e r a l , m e t a l d e t e c t o r s and m a g n e t o m e t e r s a r e most u s e f u l i n l o c a t i n g b u r i e d w a s t e s ; g r o u n d p e n e t r a t i n g r a d a r i s the technique o f c h o i c e f o r d e f i n i n g the boundary o f b u r i e d t r e n c h e s ; e l e c t r o m a g n e t i c i n d u c t i o n (EM) a n d r e s i s t i v i t y a r e t h e most u s e f u l i n d e f i n i n g plumes o f c o n d u c t i v e c o n t a m i n a n t s i n g r o u n d w a t e r ; a n d r e s i s t i v i t y and s e i s m i c t e c h n i q u e s a r e most useful i n determining geologic stratigraphy. M e t a l D e t e c t o r s . M e t a l d e t e c t o r s r e s p o n d t o changes i n e l e c t r i c a l c o n d u c t i v i t y c a u s e d by t h e p r e s e n c e o f m e t a l l i c o b j e c t s , b o t h f e r r o u s and n o n - f e r r o u s . A t t h e same t i m e , m e t a l d e t e c t o r s a r e r e l a t i v e l y i n s e n s i t i v e t o changes i n s o i l m o i s t u r e or groundwater c o n d u c t i v i t y . The m a g n i t u d e o f r e s p o n s e f r o m a metal detector i s a function of several v a r i a b l e s . 1) Target t o sensor d i s t a n c e (response f a l l s o f as the s i x t h power o f t h e d i s t a n c e ) 2) Target s i z e 3) Target o r i e n t a t i o n 4) Target geometry 5) Type o f t a r g e t m e t a l 6) M e c h a n i c a l / e l e c t r i c a l i n t e g r i t y o f the t a r g e t 7) Search c o i l s i z e The o p e r a t i o n o f s i m p l e m e t a l d e t e c t o r s i s diagrammed s c h e m a t i c a l l y i n F i g u r e 1, w h i c h shows a n i n d u c t i o n b a l a n c e
Long and Schweitzer; Risk Assessment at Hazardous Waste Sites ACS Symposium Series; American Chemical Society: Washington, DC, 1982.
Long and Schweitzer; Risk Assessment at Hazardous Waste Sites ACS Symposium Series; American Chemical Society: Washington, DC, 1982.
X - PRIMARY METHOD ( X ) - SECONDARY METHOD
LOCATION AND DEFINITION OF BURIED METALLIC OBJECTS (E.G., DRUMS, ORDINANCE)
LOCATION OF BOUNDARY DEFINITION OF BURIED TRENCHES
MAPPING OF GEOHYDROLOGIC FEATURES
MAPPING OF CONDUCTIVE LEACHATES AND CONTAMINANT PLUMES (E.G., LANDFILLS, ACIDS, BASES)
(X)
(X)
X
X
X
X
X
(X)
ELECTROMAGNETIC INDUCTION
(X)
X
X
RESISTIVITY
(X)
X
SEISMIC
X
(X)
METAL DETECTOR
POTENTIAL APPLICATIONS OF GEOPHYSICAL METHODS
GROUND PENETRATING RADAR
TABLE I .
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(X)
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8.
Figure 1. Simplified diagram of metal detector system.
Long and Schweitzer; Risk Assessment at Hazardous Waste Sites ACS Symposium Series; American Chemical Society: Washington, DC, 1982.
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device. Such a d e v i c e c o n s i s t s o f a t r a n s m i t t e r l o o p c o i l and a r e c e i v e r l o o p c o i l g e o m e t r i c a l l y a r r a n g e d i n s u c h a way t h a t a n u l l or z e r o - i n d u c t i o n c o n d i t i o n i s a c h i e v e d i n the absence of n e a r b y m e t a l o b j e c t s . When t h e c o i l s a r e p r o p e r l y a d j u s t e d , t h e r e c e i v e r i s i n s e n s i t i v e to the e l e c t r o m a g n e t i c f i e l d of the transmitter. However, a s i g n a l w i l l be d e t e c t e d i f t h e e l e c t r o m a g n e t i c f i e l d a t t h e r e c e i v e r c o i l i s a l t e r e d by t h e s u p e r p o s i t i o n of a secondary e l e c t r o m a g n e t i c f i e l d r e s u l t i n g from c u r r e n t s induced i n a nearby m e t a l l i c o b j e c t or conductive mass by t h e t r a n s m i t t e r c o i l . D e v i a t i o n s from the balance c o n d i t i o n a r e d e t e c t e d as e l e c t r i c a l s i g n a l s i n t h e r e c e i v e r and a r e e l e c t r o n i c a l l y c o n v e r t e d t o a m e t e r d e f l e c t i o n as w e l l as t o an a u d i b l e t o n e . M e t a l d e t e c t o r s t e n d t o be i n s e n s i t i v e t o b u r i e d o b j e c t s o f s m a l l c r o s s - s e c t i o n , s u c h as m e t a l r o d s . (_1) F i g u r e 2 shows p r o f i l e s t a k e n w i t h a m e t a l d e t e c t o r a t a r u r a l s i t e where i t was s u s p e c t e d t h a t drums c o n t a i n i n g d i o x i n had been dumped i n t o a t r e n c h and b u r i e d . M u l t i p l e p a r a l l e l p a s s e s were made p e r p e n d i c u l a r t o t h e s u s p e c t e d t r e n c h as p a r t o f an e f f o r t t o d e t e r m i n e t h e l o c a t i o n and q u a n t i t y o f drums i n the t r e n c h . (2) M a g n e t o m e t e r s . M a g n e t o m e t e r s c a n be u s e d t o d e t e c t p e r t u r b a t i o n s i n t h e g e o m a g n e t i c f i e l d c r e a t e d by b u r i e d f e r r o m a g n e t i c o b j e c t s s u c h as s t e e l c o n t a i n e r s o r drums, t o o l s , or scrap metal. An i n d u c e d m a g n e t i z a t i o n i s p r o d u c e d i n any m a g n e t i c m a t e r i a l w i t h i n t h e e a r t h ' s m a g n e t i c f i e l d , and t h i s i n d u c e d f i e l d i s s u p e r i m p o s e d on t h e g e o m a g n e t i c f i e l d . If s t r o n g enough, t h i s i n d u c e d f i e l d p r o d u c e s a l o c a l i z e d anomaly i n the geomagnetic f i e l d . F i g u r e 3 i s a schematic of a simple magnetometer. The i n d u c e d m a g n e t i c f i e l d o f a b u r i e d o b j e c t depends on several variables: 1) T a r g e t mass; 2) Target to sensor d i s t a n c e ; 3) T a r g e t m a t e r i a l and i t s i n t e g r i t y ; 4) Target geometry ( p r i m a r i l y l e n g t h to diameter r a t i o ) 5) Target o r i e n t a t i o n ; 6) M a g n i t u d e and d i r e c t i o n o f permanent magnetism i n t h e target A v a r i e t y of magnetometers are c u r r e n t l y a v a i l a b l e f o r d i f f e r e n t types of s u r v e y s . B o t h t o t a l f i e l d and g r a d i o m e t e r s e a r c h magnetometers are used. P r o t o n p r e c e s s i o n and c e s i u m s y s t e m s a r e u s e d f o r measurements o f t h e t o t a l m a g n e t i c f i e l d . F l u x g a t e and c e s i u m g r a d i o r a e t e r s c a n be u s e d f o r s e a r c h work. A g r a d i o m e t e r i s a d i f f e r e n t i a l magnetometer w h i c h m e a s u r e s d i f f e r e n c e s i n t h e m a g n i t u d e and d i r e c t i o n o f t h e a m b i e n t f i e l d over a f i x e d d i s t a n c e ; t h i s f i x e d d i s t a n c e i s u s u a l l y small w i t h r e s p e c t to the d i s t a n c e to the o b j e c t c r e a t i n g the magnetic a n o m a l y . An a d v a n t a g e o f some g r a d i o m e t e r s y s t e m s i s t h e i r a b i l i t y to sense v e r t i c a l f i e l d g r a d i e n t s w h i l e r e m a i n i n g i n s e n s i t i v e t o h o r i z o n t a l g r a d i e n t components. T h i s f e a t u r e
Long and Schweitzer; Risk Assessment at Hazardous Waste Sites ACS Symposium Series; American Chemical Society: Washington, DC, 1982.
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Figure 2. Metal detector data over trench with buried drums.
Long and Schweitzer; Risk Assessment at Hazardous Waste Sites ACS Symposium Series; American Chemical Society: Washington, DC, 1982.
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Figure 3.
Simplified diagram of magnetometer system.
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a l l o w s gradioraeters t o sense the v e r t i c a l f i e l d o f s u b s u r f a c e t a r g e t s i n the presence o f h o r i z o n t a l i n t e r f e r e n c e t a r g e t s such as s t e e l f e n c e s . ( 3 ) F i g u r e 4 shows m u l t i p l e p a r a l l e l p r o f i l e s t a k e n w i t h a continuous r e a d i n g gradiometer over the d r u m - f i l l e d b u r i a l t r e n c h ( t h e same t r e n c h f r o m w h i c h F i g u r e 2 was t a k e n ) . These p r o f i l e s , w h i c h add c o n f i r m a t i o n o f t h e p r e s e n c e o f drums i n t h e t r e n c h , were t a k e n i n s i d e a h i g h s t e e l f e n c e e r e c t e d a r o u n d t h e suspected b u r i a l s i t e . ( 2 ) G r o u n d - P e n e t r a t i n g R a d a r . The g r o u n d - p e n e t r a t i n g radar (GPR) s y s t e m most f r e q u e n t l y u s e d i n h a z a r d o u s w a s t e s i t e i n v e s t i g a t i o n s i s an impulse system w h i c h r a d i a t e s s h o r t - d u r a t i o n e l e c t r o m a g n e t i c p u l s e s i n t o the ground from a n a n t e n n a n e a r t h e s u r f a c e . These p u l s e s a r e r e f l e c t e d f r o m v a r i o u s i n t e r f a c e s w i t h i n t h e e a r t h and a r e p i c k e d up by t h e r e c e i v e r s e c t i o n o f t h e a n t e n n a and r e t u r n e d t o t h e c o n t r o l u n i t f o r p r o c e s s i n g a n d d i s p l a y . These r e f l e c t i o n s o c c u r a t different s o i l horizons, soil/rock interfaces, rock/air i n t e r f a c e s ( v o i d s ) , manmade o b j e c t s , o r a t a n y i n t e r f a c e w h i c h c r e a t e s a c o n t r a s t i n complex d i e l e c t r i c p r o p e r t i e s . F o r e x a m p l e , d i g g i n g a t r e n c h and f i l l i n g i t a g a i n c a n c r e a t e a d i f f e r e n c e between t h e d i e l e c t r i c p r o p e r t i e s o f t h e d i s t u r b e d e a r t h and t h o s e o f t h e u n d i s t u r b e d m a t e r i a l w h i c h c a n be s e n s e d by t h e GPR. F i g u r e 5 i s a schematic showing the v a r i o u s components o f a GPR s y s t e m . F o r p r e s e n t a t i o n o f d a t a , GPR s i g n a l s a r e p r o c e s s e d and d i s p l a y e d by a g r a p h i c r e c o r d e r . As t h e a n t e n n a i s moved a l o n g the s u r f a c e , the g r a p h i c d i s p l a y r e s u l t s i n a p i c t u r e - l i k e r e c o r d showing a c o n t i n u o u s p r o f i l e a l o n g a t r a v e r s e , v e r y s i m i l a r t o a g e o l o g i c c r o s s - s e c t i o n found a t a roadcut. U n f o r t u n a t e l y , the depth o f radar p e n e t r a t i o n i s very s i t e specific. D e p t h s o f 3 t o 10 m e t e r s a r e commonly a t t a i n e d t h r o u g h o u t t h e c o u n t r y ; 20 m e t e r p e n e t r a t i o n s have been a c h i e v e d u n d e r i d e a l c o n d i t i o n s a t some s i t e s . This depth i s reduced i f ground water i n c r e a s e s i n e l e c t r i c a l c o n d u c t i v i t y , o r i f t h e r e are s u f f i c i e n t l y high concentrations of f i n e grained m a t e r i a l s ( s i l t s or c l a y s ) present. For example, h i g h c o n c e n t r a t i o n s o f s a l t s , m o n t m o r i l l o n i t e c l a y o r l o s s e s are h i g h l y a t t e n u a t i v e of t h e r a d a r p u l s e and p e n e t r a t i o n may n o t e x c e e d one m e t e r . ( 4 ) F i g u r e 6 shows t h e c r o s s - s e c t i o n r e s u l t i n g f r o m a s i n g l e GPR t r a v e r s e a c r o s s t h e b a r r e l - f i l l e d t r e n c h f r o m w h i c h F i g u r e s 2 and 4 were t a k e n . The images p r o d u c e d by t h r e e 5 5 - g a l l o n b a r r e l s a r e i n d i c a t e d on t h e f i g u r e . Figure 7 i s a composite, c o m p a r i n g t h e t r a c e s o f F i g u r e s 2, 4, a n d 6. ( 5 ) Resistivity. The r e s i s t i v i t y method m e a s u r e s t h e e l e c t r i c a l r e s i s t i v i t y o f the g e o h y d r o l o g i c s e c t i o n , which i n c l u d e s s o i l , r o c k , and g r o u n d w a t e r . I n t e r p r e t a t i o n of these measurements p r o v i d e i n f o r m a t i o n on l a y e r i n g a n d d e p t h s o f s u b s u r f a c e h o r i z o n s a s w e l l a s l a t e r a l changes i n t h e
Long and Schweitzer; Risk Assessment at Hazardous Waste Sites ACS Symposium Series; American Chemical Society: Washington, DC, 1982.
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RISK
Figure 4.
ASSESSMENT
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HAZARDOUS WASTE
SITES
Magnetometer data over trench with buried drums.
Graphic Recorder
Antenna Sampler Circuits
Controller 5-300 Meter Cable
Bow Tie
Tape Recorder
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Radar Waveform
α ο ο •
• Ground Surface-
ι Figure 5.
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