29 Ground Water Contamination by Toxic Substances A California Assessment
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David B. Cohen Pollutant Investigations Branch, State Water Resources Control Board, Sacramento, CA 95801
Overoptimistic risk perception, coupled with inadequate risk assessment, has led to underprotective risk management of toxic chemicals in ground water. In California, soil nematicides like DBCP are a particular concern. DBCP use was banned in 1977, yet it is s t i l l found in over 2500 wells. An estimated 700,000 people in 32 towns are either drinking water with measurable levels of DBCP or have had to seek alternative water supplies. Over 50 other pesticides including 1,2-D, EDB, and aldicarb have been found in California ground water from both point and nonpoint sources. Future risk management strategies must be based on a more conservative risk perception approach. California Water Resources Control Board's ground water "hot spots" program is an example of such an approach. In s e m i - a r i d C a l i f o r n i a , ground water i s a p r e c i o u s r e s o u r c e . D u r i n g t h e p a s t decade, t h e S t a t e Water Resources C o n t r o l Board, C a l i f o r n i a ' s e n v i r o n m e n t a l p r o t e c t i o n agency f o r water q u a l i t y , has l e a r n e d t h a t we have n o t done enough t o p r e v e n t t h e growing problem of t o x i c c h e m i c a l c o n t a m i n a t i o n o f our ground water. While both i n d u s t r i a l and a g r i c u l t u r a l c h e m i c a l s have been found i n C a l i f o r n i a ground w a t e r s , p e s t i c i d e s i n j e c t e d beneath the s o i l s u r f a c e t o c o n t r o l nematodes a r e a p a r t i c u l a r c o n c e r n . The n e m a t i c i d e 1,2-dibromo-3-chloropropane (DBCP), which was banned i n C a l i f o r n i a i n 1977, i s t h e most s e r i o u s example o f t h i s problem i n C a l i f o r n i a ( 1 - 2 ) . F i g u r e 1 shows t h e i n c r e a s e between 1979 and 1984 i n t h e number o f w e l l s found t o c o n t a i n measurable q u a n t i t i e s of DBCP. As o f A p r i l 1984, 2522 w e l l s c o n t a i n e d DBCP, w i t h over h a l f t h e s e w e l l s (1455) h a v i n g c o n c e n t r a t i o n s i n e x c e s s o f 1.0 part per b i l l i o n , the c u r r e n t C a l i f o r n i a "action l e v e l " . T a b l e I l i s t s over 50 o t h e r p e s t i c i d e s (from both p o i n t and n o n p o i n t s o u r c e s ) t h a t have been i d e n t i f i e d i n ground water from 28 o f C a l i f o r n i a ' s 58 c o u n t i e s . F i g u r e 2 shows t h e g e o g r a p h i c
0097-6156/ 86/ 0315-0499$08.75/0 © 1986 American Chemical Society
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
500
EVALUATION O FPESTICIDES ING R O U N D WATER
2600 (2522)
2400
(2252)
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LU >
2200
2000
Ο 1800
LU
1600
ο
(1455)
UJ
< Ζ
1400
(1292)
i < ο ο
1200
-
LL
1000
-
800
-
Ο CO CC LU
m 3 600
>1.0 p p b (Action Level)
400
-
200
-
'79
'80
'81
'83
'84
YEAR
F i g u r e 1. DBCP i n C a l i f o r n i a (May 1979 - A p r i l 1984) .
Ground Water
- Cumulative
Summary
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
29.
COHEN
501
Ground Water Contamination by Toxic Substances
Table I.
Pesticides Detected in California Ground Water
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(Large Water Systems vs. Small Domestic Systems) No.Verified
Pesticide
N
Pesticide
o
*
Incidents
Aldicarb Aldrin
27 22
Dieldrin Dimethoate
Atrazine
2
Bentazon Benzaldehyde
1 1 4
Diphenamid Disulfoton DNBP
Chlordane Chlorpropham
1
Dacthal
4
DBCP DDD
2522 4 15
DDE DDT DEF
10 1 4
Delnav Diazinon Dichlone 1,2-Dichloropropane 1,3-Drchloropropene(cis) 1,3-Dichloropropene(tran8)
12 1 72 2 1
Verified Incidents
DNOC Dursban EDB Endosulfan
4 24 1 6 11 2 3 32 23 1
Pesticide
Omite Ordram Paraoxon P a r a t h i o n , ethyl P a r a t h i o n , methyl PCNB PCP Phorate Phthalates
Ethion Ethylene thiourea Furadan (carbofuran)
5
Sevin Simazlne
1 2
TCP Toxaphene
Heptachlor
4 3
Treflen Zytron
Endrin
Kelthane
(dicofol)
Lindane Malathion Methylene chloride Naled
18 5 4 7
No. Verified Incidents
2,4-D 2,4,5-T 2,4.5-TP TOTAL
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
2 3 1 4 1 1 38 2 4 3 9 6 5 1 4 10 4 3 2963
WATER
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E V A L U A T I O N O F PESTICIDES IN G R O U N D
F i g u r e 2. V e r i f i e d I n c i d e n t s o f Ground Water C o n t a m i n a t i o n P e s t i c i d e s ( I n c l u d i n g DBC).
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
with
29.
COHEN
Ground Water Contamination by Toxic Substances
503
d i s t r i b u t i o n o f a l l v e r i f i e d i n c i d e n t s o f ground water c o n t a m i n a t i o n by p e s t i c i d e s ( i n c l u d i n g DBCP) as o f November 1984. T h i s paper f o c u s e s on C a l i f o r n i a ' s e x p e r i e n c e s w i t h p e s t i c i d e s i n ground water, p o t e n t i a l c a u s e s , and p o s s i b l e s o l u t i o n s .
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C a l i f o r n i a ' s Water Q u a l i t y P r o t e c t i o n
Program
In 1969, C a l i f o r n i a adopted the P o r t e r - C o l o g n e A c t g i v i n g t h e S t a t e Water Resources C o n t r o l Board ( S t a t e Board) t h e a u t h o r i t y t o (1) a s s u r e t h a t a l l water d i v e r s i o n s be p u t t o a b e n e f i c i a l u s e , and (2) m a i n t a i n and enhance t h e q u a l i t y o f a l l waters o f t h e State. One major d i f f e r e n c e between f e d e r a l and s t a t e water q u a l i t y p r o t e c t i o n programs i n v o l v e s p r o t e c t i o n o f ground water. The 1972 F e d e r a l C l e a n Water A c t a d d r e s s e d s u r f a c e water q u a l i t y ( " f i s h a b l e and swimmable" by 1985), s p e c i f i c a l l y e x c l u d i n g n o n p o i n t s o u r c e a g r i c u l t u r a l r e t u r n f l o w s from r e g u l a t i o n . C a l i f o r n i a law p r o t e c t s a l l waters o f the S t a t e , i n c l u d i n g ground water and g i v e s the S t a t e Board a u t h o r i t y t o r e g u l a t e a l l s o u r c e s o f c o n t a m i n a t i o n including pesticides i n a g r i c u l t u r a l runoff. H i s t o r i c a l l y , such n o n p o i n t s o u r c e s have r a r e l y been r e g u l a t e d by t h e S t a t e and R e g i o n a l Boards because o f t h e d i f f i c u l t y i n t r a c i n g problem e v e n t s t o an unknown number o f d i f f u s e s o u r c e s . The S t a t e i s s u b d i v i d e d a l o n g d r a i n a g e b a s i n b o u n d a r i e s i n t o n i n e r e g i o n s , each w i t h i t s own R e g i o n a l Water Q u a l i t y C o n t r o l Board ( F i g u r e 3 ) . The r e g i o n a l b o a r d s have t h e a u t h o r i t y t o (1) i s s u e waste d i s c h a r g e r e q u i r e m e n t s , (2) m o n i t o r water q u a l i t y , (3) take enforcement a c t i o n s , and (4) adopt n a r r a t i v e o r n u m e r i c a l water q u a l i t y objectives i n t o basin plans. A t y p i c a l basin plan narrat i v e o b j e c t i v e s t a t e s t h a t "the d i s c h a r g e o f p e s t i c i d e s t o waters o f t h e r e g i o n o r a t l o c a t i o n s where the waste may s u b s e q u e n t l y r e a c h waters o f t h e r e g i o n i s p r o h i b i t e d " . In o r d e r t o p r o t e c t ground water, t h e S t a t e Board i n 1972 adopted r e g u l a t i o n s g o v e r n i n g hazardous waste d i s p o s a l t o l a n d . These r e g u l a t i o n s (Subchapter 15 o f the C a l i f o r n i a Water Code) c l a s s i f i e d both wastes and s i t e s . Wastes were c a t e g o r i z e d on t h e b a s i s o f t h e r e l a t i v e h a z a r d t o h e a l t h and t h e environment, w h i l e s i t e s were p r i o r i t i z e d a c c o r d i n g t o p o t e n t i a l f o r l e a c h i n g and ground water c o n t a m i n a t i o n . As t h r e a t s from b i o l o g i c a l p o l l u t a n t s i n s u r f a c e waters l e s s e n , the awareness o f t h r e a t s from t o x i c c h e m i c a l s i n c r e a s e s . Hardly a week goes by w i t h o u t a new r e p o r t o f t o x i c o r g a n i c c h e m i c a l s i n a community water s u p p l y o r o t h e r water r e s o u r c e . DBCP
(1,2-Dibromo-3-chloropropane)
The most w i d e s p r e a d p e s t i c i d e c o n t a m i n a t i o n o f ground water i n C a l i f o r n i a (and, p o s s i b l y , the n a t i o n ) has o c c u r r e d t h r o u g h use o f DBCP. The c h e m i c a l was f i r s t d i s c o v e r e d i n C a l i f o r n i a ground water i n 1979 by t h e C e n t r a l V a l l e y R e g i o n a l Board. Eight years a f t e r i t s use was banned, more DBCP-contaminated w e l l s a r e s t i l l b e i n g discovered. DBCP i n some w e l l waters was a t h i g h e r l e v e l s i n 1984 than when f i r s t d i s c o v e r e d i n 1979 ( F i g u r e 4 ) . Many o f t h e s e w e l l s have been shut down p e r m a n e n t l y , w h i l e o t h e r s a r e o n l y used on an emergency b a s i s o r when DBCP c o n c e n t r a t i o n s d e c r e a s e below 1 ppb.
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
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E V A L U A T I O N O F PESTICIDES IN G R O U N D
F i g u r e 3.
R e g i o n a l Water Q u a l i t y C o n t r o l
Boards.
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
WATER
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29.
COHEN
Ground Water Contamination by Toxic Substances
505
Of 8,190 C a l i f o r n i a w e l l s m o n i t o r e d by November 1984, 30.8 p e r c e n t were found t o c o n t a i n DBCP. F r e s n o County had the h i g h e s t p e r c e n t a g e (41.3 p e r c e n t ) and g r e a t e s t number (1,696) o f DBCP c o n t a m i n a t e d w e l l s . In some a r e a s o f F r e s n o County, over h a l f the p r i v a t e w e l l s sampled c o n t a i n e d DBCP above the DHS a c t i o n l e v e l o f I ppb. C a l i f o r n i a has spent over $10 m i l l i o n i n Fresno County a l o n e to r e h a b i l i t a t e DBCP-contaminated ground water s u p p l i e s . Many o f the worst p o l l u t i o n problems were found i n s m a l l or p r i v a t e r u r a l systems where a w e l l s e r v e s one or more homes. Table I I compares t h e degree o f DBCP-contamination f o r both l a r g e p u b l i c water systems (>200 c o n n e c t i o n s ) and s m a l l e r systems (5-200 c o n n e c t i o n s ) i n 11 C a l i f o r n i a c o u n t i e s . Large water systems had 14.6 p e r c e n t o f t h e i r w e l l s c o n t a m i n a t e d w i t h DBCP compared t o 33.6 p e r c e n t f o r s m a l l and d o m e s t i c water systems which f r e q u e n t l y pump from s h a l l o w e r , more v u l n e r a b l e a q u i f e r s . By comparison, a r e c e n t l y i n a u g u r a t e d s t a t e w i d e m o n i t o r i n g program f o r over 40 t o x i c c h e m i c a l s i n l a r g e community w e l l s (AB 1803) found t o x i c o r g a n i c c h e m i c a l s i n 82 o f 320 systems (25.6 p e r c e n t ) . (3) DBCP c o n c e n t r a t i o n s i n some F r e s n o County d o m e s t i c w e l l s sampled between 1979-1984 have f l u c t u a t e d s e a s o n a l l y by an o r d e r o f magnitude. F i g u r e 5 shows DBCP c o n c e n t r a t i o n s i n one w e l l f l u c t u a t e d between 3 t o 33 p a r t s per b i l l i o n w i t h i n s i x months d u r i n g 1981. Sample c o l l e c t i o n and a n a l y t i c a l methods were unchanged d u r i n g t h i s p e r i o d . A l t h o u g h the reasons f o r t h i s v a r i a b i l i t y a r e not y e t c l e a r l y u n d e r s t o o d , t h e s e examples demonstrate the need t o c o n t i n u e m o n i t o r i n g even a f t e r c o n c e n t r a t i o n s f a l l "below detection limits". Plumes o f DBCP c o n t a m i n a t e d ground water can move u n p r e d i c t a b l y through a q u i f e r s t o r e a c h p r e v i o u s l y u n c o n t a m i nated monitoring w e l l s . These r e t r o s p e c t i v e DBCP m o n i t o r i n g d a t a a r e p r e s e n t l y b e i n g t r a n s f e r r e d t o computer f i l e s . When t h i s work i s completed, a n a l y s i s o f s p a t i a l and temporal t r e n d s and p o s s i b l e c o r r e l a t i o n s w i t h s o i l and water p r e d i c t i v e f a c t o r s w i l l be attempted. C a l i f o r n i a i s f o r t u n a t e i n h a v i n g a mandatory use r e p o r t i n g system f o r r e s t r i c t e d p e s t i c i d e s . ( 4 ) Computer t a p e s c o n t a i n i n g the raw d a t a from t h i s program a r e t r a n s f e r r e d t o the U n i v e r s i t y of C a l i f o r n i a a t D a v i s , which has, w i t h S t a t e Board s u p p o r t , d e v e l o p e d a computer program f o r mapping p e s t i c i d e use i n f o r m a t i o n g e o g r a p h i c a l l y (by c o u n t y , r e g i o n , or the S t a t e ) and t e m p o r a l l y (by s e a s o n , y e a r , or c u m u l a t i v e y e a r s ) . F i g u r e 6, which shows r e p o r t e d C a l i f o r n i a use o f DBCP f o r 1972-1977, i s an example o f that c a p a b i l i t y . U n f o r t u n a t e l y , not a l l p e s t i c i d e use was r e q u i r e d t o be r e p o r t e d d u r i n g t h i s p e r i o d . DBCP was o n l y r e q u i r e d t o be r e p o r t e d s h o r t l y b e f o r e i t s use was banned i n 1977. The Department of Food and A g r i c u l t u r e has t h e r e f o r e e s t i m a t e d a c t u a l use t o be a p p r o x i m a t e l y t h r e e times r e p o r t e d use. The b e s t e s t i m a t e o f a c t u a l c u m u l a t i v e DBCP use between 1957 and 1977 i s i n e x c e s s o f 50 m i l l i o n pounds. D e s p i t e the i n c o m p l e t e n e s s o f p a s t p e s t i c i d e use r e p o r t s , t h i s p e s t i c i d e mapping c a p a b i l i t y i s an i m p o r t a n t t o o l i n f o c u s i n g S t a t e Board f i e l d m o n i t o r i n g e f f o r t s on a r e a s o f greatest potential risk. A p r o s p e c t i v e f i e l d s t u d y o f DBCP movement (both h o r i z o n t a l and v e r t i c a l ) through s o i l t o ground water has been proposed by r e s e a r c h e r s a t the U n i v e r s i t y o f C a l i f o r n i a , D a v i s . A particularly
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
EVALUATION O F PESTICIDES IN G R O U N D WATER
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506
YEAR
F i g u r e 4.
DBCP C o n c e n t r a t i o n s
i n E s c a l o n M u n i c i p a l W e l l No. 3.
Table Π . Percent of Wells Contaminated with DBCP (Point and Nonpoint Source-1884) County
Large Systems
Small Systems
TOTAL
19.1
43.4
41.3
KERN
5.9
23.3
15.9
MADERA
2.7
22.9
20.7
MERCED
22.7
23.5
23.4
TULARE
10.4
29.4
23.8
SAN
19.9
19.4
19.6
16.2
19.9
18.5
2.7
9.1
FRESNO
JOAQUIN
STANISLAUS RIVERSIDE SAN
BERNADINO
SUTTER BUTTE TOTAL
5.0
-
35.8
44.4
52.4
-
33.3
33.3
14.6
33.6
30.8
35.8 100.0
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
In Evaluation of Pesticides in Ground Water; Garner, W., et al.; ACS Symposium Series; American Chemical Society: Washington, DC, 1986.
Downloaded by UNIV OF CALIFORNIA SAN DIEGO on August 25, 2015 | http://pubs.acs.org Publication Date: July 17, 1986 | doi: 10.1021/bk-1986-0315.ch029
-
Ο
Ι I
δ-