United States
                     Environmental Protection
                     Agency
Environmental Monitoring and
Support Laboratory
Cincinnati OH 45268
                     Research and Development
EPA/600/S4-85/050 Sept. 1985
v°/EPA          Project Summary

                     Evaluation  of  10  Pesticide
                     Methods
                     T. M. Engel, J. S. Warner, and W. M. Cooke
                       Ten pesticide analysis methods were
                     evaluated. The compounds listed in
                     each method were analyzed in tripli-
                     cate at two concentration  levels in
                     reagent water and POTW effluent. Each
                     method was performed as written with
                     only minor modifications. If a cleanup
                     procedure was included in the analysis
                     method, all analyses were performed
                     with and without the cleanup step.
                       Resultant data reported included es-
                     timated detection limits (EDLs) in
                     reagent water and recovery data from
                     reagent water and POTW effluent for
                     each compound. Suggestions for
                     method improvements were included
                     in the report where necessary.
                       This Project Summary was devel-
                     oped by EPA's Environmental Monitor-
                     ing and Support Laboratory, Cincinnati,
                     OH, to announce key findings of the re-
                     search project that is fully documented
                     in a separate report of the same title
                     (see Project Report ordering informa-
                     tion at back).

                     Introduction
                      Ten pesticide analysis methods were
                     evaluated; a description of the methods
                     and the compounds included in those
                     methods are listed in Table 1. The com-
                     pounds included in each method were
                     analyzed in triplicate at two concentra-
                     tion levels in reagent water and POTW
                     effluent. Each method was performed
                     as written with  only minor modifica-
                     tions as approved by the EPA Project
                     Officer. If a cleanup procedure was in-
                     cluded in the analysis method, all analy-
                     ses were  performed with and without
                     the cleanup step.
                      Resultant data reported included esti-
                     mated detection limits (EDLs) in reagent
                     water and  recovery data from reagent
water and POTW effluent for each com-
pound  before and after the optional
cleanup step. Suggestions for method
improvements were offered where
warranted.

Results
  A summary of the EDL and recovery
data obtained during the evaluation of
the 10  pesticide methods is given in
Table 2. Methods 641, 643, and 645
were found to yield  acceptable results
as written. Method 641.1 was not ac-
ceptable due to low recoveries  of
ethoxyquin, presumably due to adsorp-
tion of the ethoxyquin to paniculate ma-
terial prior to filtration of the sample for
HPLC analysis. Method 642 was mar-
ginally  acceptable;  recoveries of bi-
phenyl  and o-phenylphenol were  low,
possibly due to the rigorous conditions
needed to concentrate sample extracts.
Method 632.1 was acceptable for two of
the compounds, napropamide  and
propanil, but was not acceptable for the
determination of carbaryl (carbaryl re-
coveries were low and dependent upon
sample  matrix and carbaryl concentra-
tion). Method 644 was not acceptable;
picloram  recoveries were low, pre-
sumably due to incomplete extraction
of the picloram from the water matrix.
The extraction and analysis portions of
Method 614.1 were found to be accept-
able for dioxathion,  EPN, ethion,  and
terbufos. The silica gel cleanup proce-
dure included in Method 614.1  was not
acceptable; compound recoveries were
decreased by 50 percent or more when
the cleanup procedure was used.
Method 646 was found to be acceptable
for the  determination of basalin  and
marginally acceptable for the determi-
nation of  CDNB and dinocap.  Method

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Table 1.    Pesticide Method Information
Method
Number
641
647.7
642
642
643
632.7
632.7
632.7
632.7
644

614.1
614.1
674.7
674.7
645
645
645
645
645
645
646
646
646
608.2
608.2
608.2
608.2
608.2
Compound(s)
Thiabendazole
Ethoxyquin
Biphenyl
0-Phenylphenol
Bentazon
Carbaryl
Napropamide
Propanil
Vacor
Picloram

Dioxathion
EPN
Ethion
Terbufos
Alachlor
Butachlor
Diphenamid
Lethane
Norflurazon
Fluridone
Basalin
CDNB
Dinocap
Chlorothalonil
DCPA
Dichloran
Methoxychlor
Permethrin
Extraction
Method
None
None
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
None
Separatory funnel

Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Separatory funnel
Cleanup
Method
Filtration
Filtration
None
None
None
None
None
None
None
Backextraction
with base
Silica gel
Silica gel
Silica gel
Silica gel
Florisil
Florisil
Florisil
Florisil
None
None
Florisil
Florisil
Florisil
Silica gel
Florisil
Florisil
Silica gel
Silica gel
Analysis
Method
HPLC-Fluorescence
HPLC-Fluorescence
HPLC-UV
HPLC-UV
HPLC-UV
HPLC-UV
HPLC-UV
HPLC-UV
None
HPLC-UV

GC-NPD
GC-NPD
GC-NPD
GC-NPD
GC-NPD
GC-NPD
GC-NPD
GC-NPD
GC-NPD
GC-NPD
GC-ECD
GC-ECD
GC-ECD
GC-ECD
GC-ECD
GC-ECD
GC-ECD
GC-ECD
A standard of vacor could not be obtained; Method 5 was not evaluated for vacor.
608.2 was found to  be acceptable for
cis- and trans-permethrin, but was not
acceptable for the determination of
DCPA, methoxychlor, chlorothalonil,
and dicloran. Recoveries of DCPA and
methoxychlor were low and concentra-
tion and matrix dependent. Recoveries
of chlorothalonil and dicloran  could not
be determined because of the presence
of interferences.

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Table 2.    Summary of Data from Evaluation of W Pesticide Analysis Methods

                                                      Recovery from Reagent Water. %ldl
Recovery from POTW Effluentldl
Method
Number Compound
641
641.1
642
642
643
632.1
632.1
632.1
644
614.1
614.1
614.1
614.1
645
645
645
645
645
645
646
646
646
608.2
608.2
608.2
608.2
608.2
608.2
Thiabendazole
Ethoxyquin
Biphenyl
O-Phenylphenol
Bentazon
Carbaryl
Napropamide
Propanil
Picloram
Dioxathion
EPN
Ethion
Terbufos
Alachlor
Butachlor
Diphenamid
Lethane
Norflurazon
Fluridone
Basalin
CDNB
Dinocap
Chlorothalonil
DCPA
Dicloran
Methoxychlor
Cis-permethrin
Trans-permethrin
EDL,
1.7
6.3
0.04
0.01
1.1
1.2
0.02
0.3
0.3
0.5
12
0.3
0.02
0.2
0.2
0.2
0.1
0.02
0.6
0.0005
0.0005
0.1
0.001
0.003
0.002
0.4
0.2
0.2
Spike Level, pg/L
Low
10
6.2
2.5
5.0
10
2.0
6.0
0.2
3.0
10
10
10
10
10
10
10
10
10
10
0.1
0.1
0.1
0.02
0.02
0.01
0.1
1.0
1.0
High
100
62
25
50
100
20
60
2
30
100
100
100
100
100
100
100
100
100
100
1
1
1
0.2
0.2
0.1
7
70
10
Before Cleanup
Low
93 ± 3
100 + 32
74+2
73 ± 4
92+2
52+ 10
103 ± 2
79+6
N.D.
76+ 10
120+ 6
120+ 5
90+3
96+3
96+4
93+6
93 ± 6
69 ± 10
49 ± 76
738 ± 12
91+8
78+7
llcl
128 + 18
1
57+ 1
94+9
111 ± 4
High
81+5
82+6
51 + 11
60+5
81 + 10
83+ 13
102 + 2
99+3
N.D.
78+2
120+ 4
95+2
84+ 1
94+2
93+ 1
94+2
100+ 1
92+ 1
81 + 15
113+ 4
69+5
77+4
1
94+11
1
106 + 12
91+2
98+3
After Cleanup
Low
N.C.ia>
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.D.
43+ 7
N.D.
54 ± 8
N.D.
96 ± 3
95+3
95+2
97+2
69 ± 6
N.C.
126 ± 8
89 ± 6
26+3
1
73 + 25
1
37+8
91+6
83+ 72
High
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.D.
58+6
65+ 14
78+ 11
42+ 13
94+3
93+2
97 ± 3
99' ± 4
60+6
N.C.
109 ± 10
71 + 5
72+ 14
1
62+5
1
86+ 72
128 ± 77
108 ± 13
Before Cleanup
Low
96+5
19 + 14
56+4
69+2
94+7
N.D.
96+7
85+11
52+9
87 ± 15
85+2
94+5
94 ± 5
109 ± 1
103+ 1
105+ 1
120 ± 2
107 ± 1
124+ 6
94+6
78+2
76 ±40
1
N.D.
1
47 + 72
89 ± 8
85+2
High
100 ±
58 +
61 +
82 +
76 +
28 +
94 +
77 +
71 ±
91 ±
110±
86 +
77 +
102 ±
100 ±
103 +
123 ±
108 ±
777 ±
773 ±
71 ±
72 +
1
62 +
1
99 +
85 +
90 ±
2
1
1
15
2
16
3
7
0
3
6
5
3
1
1
1
1
2
2
2
2
3

5

2
3
2
After Cleanup
Low
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
58+4
67+6
N.D.
59+ 72
57+4
105 ± 3
104 ± 5
95+3
108+ 4
76 ±77
N.C.
74+3
76+4
123 ± 53
1
71 + 5
1
40 + 27
97 ± 14
41 + 11
High
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
N.C.
68+3
74+3
62+4
79+3
54+8
97+3
95+2
94+4
106+ 3
65+ 17
N.C.
108+ 3
70+2
80+ 10
1
76+2
1
90 + 14
98 + 27
95 + 29
(alN.C. = No cleanup procedure included in this method.
N.D. = Not detected.
MI - Presence of interferences precluded determination of compound in sample.
ld>Standard deviation is included.

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     Tina M. Engel, J. Scott Warner, and W. Marcus Cooke are with Battelle Columbus
       Laboratories, Columbus, OH 43201.
     Thomas A. Presshy is the EPA Project Officer (see below).
     The complete report, entitled "Evaluation of 10 Pesticide Methods," (Order No. PB
       85-238 608/AS; Cost: $14.50, subject to change) will be available only from:
             National Technical Information Service
             5285 Port Royal Road
             Springfield, VA 22161
             Telephone: 703-487-4650
     The EPA Project Officer can be contacted at:
             Environmental Monitoring and Support Laboratory
             U.S. Environmental Protection Agency
             Cincinnati, OH 45268
United States
Environmental Protection
Agency
Center for Environmental Research
Information
Cincinnati OH 45268
Official Business
Penalty for Private Use $300
EPA/600/S4-85/050
           0000329   PS
                                          AGENCY

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