Review of Pyrethroid, Fipronil and Toxicity Monitoring Data

Transcription

Review of Pyrethroid, Fipronil and Toxicity
Monitoring Data from California Urban Watersheds
Prepared for the California Stormwater Quality Association
(CASQA)
Prepared by:
Armand Ruby
Armand Ruby Consulting
July 10, 2013
Preface and Acknowledgements
This investigation and the production of this report were funded by the California Stormwater
Quality Association (CASQA) and the County of Sacramento. The work effort was coordinated
through and performed with the assistance of the CASQA Pesticides Subcommittee, particularly
subcommittee Co-Chairs Dave Tamayo and Jamison Crosby, as well as Kelly Moran of TDC
Environmental, who provided the majority of the new data sources and carefully reviewed the
draft documents.
This investigation includes literature and data sources (including unpublished data) available
from public agencies and other reputable sources with documented quality control, as well as
from sources published in the scientific literature. The responsibility for the accuracy and
veracity of the various study results rests with the original authors. This compilation is as
complete as was feasible as of early 2013, but almost certainly does not include every relevant
study.
This report was prepared by:
Armand Ruby
Armand Ruby Consulting
303 Potrero St., #43-204
Santa Cruz, CA 95060
831-477-1214
Page ii Executive Summary
In recent years, numerous studies have documented the presence of pyrethroid pesticides and
fipronil, as well as pesticide-caused toxicity, in both surface waters and sediments in California’s
urban waterways. This report compiles and summarizes chemistry data from monitoring
performed in urban areas of California for pyrethroid and fipronil pesticides, as well as related
toxicity testing results, covering the ten year period from 2003-2012. Over 9200 pyrethroid
sample analysis results and over 3200 fipronil results are evaluated and summarized.
Over the past ten years, pyrethroid pesticides have become the predominant group of chemicals
deployed for insect control in urban areas in California (TDC Environmental, 2010b), and are the
primary cause of toxicity in urban water bodies in the state (Anderson et al., 2011). The
pyrethroids are synthetic versions of the naturally-occurring pyrethrins, but are more toxic and
longer-lasting when released into the environment.
As state and federal regulatory actions have begun to address the widespread impacts of urban
pyrethroid uses, alternative insecticides, particularly fipronil, are also of increasing concern
(TDC Environmental, 2007). Fipronil has four relatively stable degradates that may contribute to
aquatic toxicity. For that reason, this report also summarizes the results of recent monitoring for
fipronil and its degradates.
Key Findings – Pyrethroids
Bifenthrin, considered to be the leading cause of pyrethroid-related toxicity in urban areas (c.f.,
Weston et al., 2005; Amweg et al., 2006; Holmes et al., 2008, TDC Environmental, 2006), was
detected most frequently of all the pesticides evaluated, in both water and sediment. Bifenthrin
was detected in 69% in sediment samples and 64% in water samples.
Detection rates were generally higher for pyrethroids in sediment than in water. Permethrin was
the most extreme case of this difference, detected in 50% of sediment samples but only 16% of
water samples. Overall, pyrethroids were detected at a rate of 31% in sediments and 24% in
water samples.
Pyrethroids were commonly found at concentrations exceeding levels known to cause toxicity to
sensitive aquatic organisms in water. The average reported concentrations of bifenthrin,
cyfluthrin, cyhalothrin, cypermethrin and permethrin in water samples range from approximately
one to more than three orders of magnitude above the non-regulatory chronic criteria values
published by UC Davis. Maximum reported concentrations of these five pyrethroids range from
two to more than four orders of magnitude higher than the UC Davis acute criteria values.
For the seven pyrethroids for which sediment toxicity (LC50) values are available, the average
concentrations reported in this summary would be substantially greater than the published
LC50s, following organic carbon normalization. This means that, under average conditions in
urban waterways in California, these pesticides are typically present in sediments at levels toxic
to sensitive aquatic macroinvertebrates such as Hyalella azteca.
Page iii These comparisons may understate the actual potential for pyrethroids to cause toxicity to
sensitive aquatic organisms, because they do not account for concurrent exposures to multiple
pyrethroids. Multiple pyrethroids typically were found in each sample in the summarized
chemistry studies, in both water and sediments. Because pyrethroid toxicity is generally
understood to be additive (c.f., Trimble et al., 2009), the actual in-situ toxicity estimated from
chemistry results should account for the mixtures of pyrethroids found.
Key Findings – Fipronil and Degradates
Fipronil was detected in 39% of water samples tested from studies evaluated for this summary,
and 19% of sediment samples. This contrasts with the pattern for most pyrethroids, for which
there were typically higher percent detections in sediment. Presumably this reflects fipronil’s
lower KOW, and/or fipronil’s relatively higher solubility in water.
The fipronil degradates as a group were detected analytically in 24% of the water samples tested
from studies evaluated for this study, and in 35% of sediment samples. This pattern is similar to
that of the pyrethroids.
Published aquatic toxicity values for fipronil are in the sub-ppb (µg/L) range (c.f., Gunasekara
and Troung, 2007 and Mize et al., 2008). Maximum observed levels of fipronil and its
degradates in water samples were higher than these LC50 values.
Key Findings – Toxicity
Toxic effects are documented in both water and sediment in urban waterways throughout
California. Effects of pyrethroids on aquatic organisms are widespread throughout the aquatic
environment, as documented in studies involving water column toxicity testing, sediment
toxicity testing, and tissue analysis. Of the 25 toxicity studies that were summarized, all reported
some level of toxicity for one or more organisms tested.
Research has for some time now indicated widespread sediment toxicity in urban areas of
California (c.f., Amweg et al., 2005, Amweg et al., 2006, Anderson et al., 2011, Holmes et al.,
2008, Weston et al. 2005), with pyrethroids often identified as the apparent cause of the toxicity.
Recent research also highlights the toxic effects of pyrethroids in water column samples. For
example, Weston and Lydy (2012) found toxicity in a majority of urban creek and river samples
tested during 2009-10 rain events. Toxicity Identification Evaluations (TIEs) and water
chemistry testing identified pyrethroids as the principal cause of the water column toxicity.
Geographical Summary
Evidence of the presence and effects of pyrethroids and fipronil, and associated toxic effects in
urban watercourses, is widely distributed geographically throughout urbanized areas of the state
of California. This review identified such data from the north coast, Lake Tahoe region, San
Francisco Bay Area, Central Valley, Central Coast, and both coastal and inland areas of southern
California. Pyrethroid-related toxicity has been documented in nearly every major urban
watershed in the state and in eight of the nine California Water Board regions.
Page iv TABLE OF CONTENTS
Preface and Acknowledgements
Executive Summary
Background and Introduction
Scope of Review and Approach
Findings
Recommendations
Conclusions
References
Appendix
Appendix
Appendix
Appendix
ii
iii
1
5
6
19
19
20
A: “Study Summaries by Author” Table
B: “Results Summaries by Geography” Table
C: “Chemistry Results Summary” Table
D: “Toxicity Results Summary” Table
Page v Background and Introduction
Legal uses of some registered pesticides have been found to result in adverse impacts to water
quality and aquatic life in receiving waters within urban areas (see summary and references in
TDC Environmental, 2010a). Over the past ten years, pyrethroid pesticides have become the
predominant group of chemicals deployed for insect control in urban areas in California (TDC
Environmental, 2010b). During this period, observations of pyrethroids and pyrethroid-caused
toxicity in urban runoff and receiving waters have multiplied, increasingly resulting in listings of
urban waterways on the Clean Water Act Section 303(d) List of Impaired Waters for California
(the “303(d) List”; State Water Resources Control Board, 2011).
Urban pyrethroid use increased dramatically beginning in the early 2000’s, when most urban
uses of the organophosphate pesticides diazinon and chlorpyrifos were curtailed by the United
States Environmental Protection Agency (USEPA). In response, other pesticides, principally
pyrethroids, were substituted as the active ingredients most commonly used for urban pest
management. The pyrethroids are synthetic versions of the naturally-occurring pyrethrins, but are
more toxic and longer-lasting when released into the environment. In recent years, numerous
studies have documented the presence of pyrethroid pesticides and pesticide-caused toxicity in
both surface waters and sediments in California’s urban waterways. This report compiles and
summarizes those findings.
Within urban areas, pesticides are often applied directly and intentionally to impervious surfaces,
and applications to impervious surfaces are considered to be the controlling factor in urban
runoff contributions to receiving water toxicity (Moran and TenBrook, 2011). The relatively low
aqueous solubility and high octanol-water partition coefficient (KOW) of most pyrethroids
indicate that these chemicals are likely to partition to suspended particulates in runoff and
accumulate in the sediments of receiving waters. Studies in California waterways have shown
that sediments contaminated with pyrethroid pesticides are frequently toxic to sediment-dwelling
organisms (c.f., Weston et al., 2005; Amweg et al., 2006; Holmes et al., 2008). However, as
documented in this report, pyrethroid pesticides are commonly found in both the waters and
sediments of urban watercourses throughout California.
With nearly 700 pyrethroid products available to professional pest control operators and
consumers in California, it is common for multiple pyrethroids to be present in the water and
sediments of urban receiving waters, as shown by numerous studies summarized in this report.
Studies involving urban monitoring data have demonstrated that mixtures of pyrethroids are
contributing to pyrethroid-related toxicity in both water and sediments in urban creeks, and
pyrethroid toxicity is generally considered to be additive in such mixtures (c.f., Trimble et al.
2009, Anderson et al., 2011).
As state and federal regulatory actions have begun to address the widespread impacts of urban
pyrethroid uses, replacement insecticides, particularly fipronil, are also of increasing concern
(TDC Environmental, 2007). For that reason, this report also summarizes the results of recent
monitoring data for fipronil and its degradates.
Page 1 Table 1 provides a summary of available water column toxicity information pertaining to
pyrethroid pesticides, with references. What is most notable about the information presented in
Table 1 is that the pyrethroids are generally toxic to the most sensitive aquatic arthropods at
extremely low levels – generally at concentrations in the single-digit (or lower) nanograms per
liter (ng/L) (parts per trillion) range. As shown in Table 1, toxicity studies typically identify the
LC50, the concentration that is lethal on average to 50% of the test organisms, and/or the EC50,
the concentration at which a sub-lethal effect is observed on average to 50% of the test
organisms. The Toxicity Values shown in Table 1 illustrate the greater sensitivity of Hyalella
azteca to pyrethroids compared to Ceriodaphnia dubia, the test species most commonly used to
identify water toxicity due to organophosphate pesticides.
USEPA has not developed recommended water quality criteria for the protection of aquatic life
for pyrethroids (or for many other current-use pesticides), as it has for other common water
pollutants. Therefore Table 1 summarizes other, non-regulatory information that can be used as
comparison values to evaluate the data compiled for this report. The available comparison values
include water quality criteria values developed by UC Davis, as described below, as well as
USEPA Aquatic Life Benchmark values.
To address recent pyrethroid-related additions to the 303(d) List within the Sacramento and San
Joaquin River watersheds, the Central Valley Regional Water Quality Control Board (RWQCB)
is developing a Basin Plan amendment to establish water quality objectives and Total Maximum
Daily Loads (TMDLs) for waterbodies that are listed for pyrethroids on the 303(d) list, and a
program of implementation for the control of pyrethroid pesticide discharges. This effort is part
of a broader program to establish water quality objectives and a program of implementation for
the control of pesticides that are impacting or could potentially impact aquatic life uses in surface
waters in the Sacramento and San Joaquin River watersheds of the Central Valley, including the
Delta. To support the development of pesticide water quality objectives and TMDLs, the Central
Valley RWQCB contracted with the Environmental Toxicology Department of the University of
California, Davis (UC Davis) to develop and evaluate a methodology for development of aquatic
life criteria. Under this contract, to date UC Davis has developed acute and chronic criteria
values for five pyrethroid pesticides, as shown in Table 1. The Central Valley RWQCB is still in
the process of determining whether or how to make use of the UC Davis criteria values in the
development of pyrethroid TMDLs for Central Valley watersheds. The context for the
development of these criteria is explained in the “Sacramento and San Joaquin River Watersheds
Pesticide Basin Plan Amendment Fact Sheet” (Central Valley RWQCB, 2006).
Table 2 provides the available water column toxicity information for fipronil and its principal
degradate compounds, as well as the corresponding USEPA Aquatic Life Benchmarks.
There are limited sediment toxicity values available for pyrethroids and fipronil/degradates, and
no corresponding comparison values for sediment (UC Davis criteria or USEPA aquatic life
benchmarks). The available published sediment toxicity LC50 values are included for
pyrethroids in Table 5 and for fipronil/degradates in Table 7.
Page 2 Table 1. Pyrethroids Water Column Toxicity and Comparison Values (ng/L)
Species
Bifenthrin
Cyfluthrin
Cypermethrin
Deltamethrin
Esfenvalerate
LambdaCyhalothrin
Permethrin
Tralomethrin
Fresh Water Toxicity Values
Hyalella azteca
7.5
2.4
2.5
8
21.1
96-hr LC50
(lethal)
Hyalella azteca
3.3
1.9
1.7
2.3
96-hr EC50
(sub-lethal effects)
Ceriodaphnia dubia
70
140
300
550
48-hr LC50
(96-h)
(lethal)
Salt Water Toxicity Values
Americamysis bahia
4
2.4
5
1.7
38
20
(Mysidopsis bahia)
96-hr EC50
(sub-lethal effects)
Comparison Values
U.C. Davis acute
4
0.3
1
1
10
criterion value (1-hr)
U.C. Davis chronic
0.6
0.05
0.2
0.5
2
criterion value (96-hr)
Lowest USEPA
1.3
7
69
4.1
17
2
1.4
4.4
Pesticide Aquatic life
benchmark
Notes for Table 1:
Compiled by TDC Environmental, 11/30/11; data not verified for this report.
Note: No USEPA water quality criteria exist for any pyrethroid.
No data are available for sensitive aquatic species for these pyrethroids (therefore excluded from table): Allethrins, tau-fluvalinate, tetramethrin.
Pyrethroids excluded because they are not used in urban areas: fenvalerate, fenpropathrin.
Pyrethroid toxicity is usually additive. Toxicity usually correlates with the sum of toxic units (sum of pyrethroid concentrations divided by their toxicity values).
Sources for Toxicity Values: Werner and Moran, 2008; Weston and Jackson, 2009; Mokry and Hoagland, 1990; Maund et al., 1998; Anderson et al., 2006.
UC Davis criteria development reports (Brander et al., 2010; Fojut et al., 2010; Fojut and Tjeerdema, 2010; Fojut et al., 2011a; Fojut et al., 2011b) are available
on the Central Valley Regional Water Quality Control Board website: http://tinyurl.com/2etvvg3
U.S. EPA Aquatic Life Benchmarks website: http://www.epa.gov/oppefed1/ecorisk_ders/aquatic_life_benchmark.htm
Page 3 Table 2. Fipronil and Degradates Water Column Toxicity and Comparison Values (ng/L)
Species
Fipronil
Fresh Water Toxicity Values
Lepomis
25,000 macrochirus
83,000 a
96-hr LC50
Chironomus tentans
410 c
96-hr LC50
Fipronil
Sulfone
Fipronil
Sulfide
25,000 a
720 c
Fipronil
Desulfinyl
Fipronil
Desulfinyl
Amide d
20,000 a
2,130 c
200,000 c
Salt Water Toxicity Values
Americamysis bahia
96-hr LC50
140 a
1,500 b
Comparison Values
Lowest U.S. EPA
Aquatic Life
Benchmark
11
37
110
590
Notes for Table 1:
Compiled by TDC Environmental; data not verified for this report.
Sources for Table 2:
a = Gunasekara and Troung, 2007 (DPR)
b = Konwick et al., 2005
c = U.S. EPA, 2011. Registration Review – Preliminary Problem Formulation for Ecological Risk and
Environmental Fate, Endangered Species, and Drinking Water Assessments for Fipronil.
d = no comparison value data available for this compound
U.S. EPA Aquatic Life Benchmarks website:
http://www.epa.gov/oppefed1/ecorisk_ders/aquatic_life_benchmark.htm
Page 4 Scope of Review and Approach
This report summarizes available chemistry data for pyrethroid pesticides and for fipronil and its
degradates, as well as related results of toxicity testing, from monitoring performed in urban
areas of California. The current report updates and expands upon the initial Pyrethroids Data
Compilation produced for CASQA in 2008 (Ruby, 2008). Data from predominantly agricultural
areas were excluded from the summaries. Otherwise, no attempt was made to distinguish the
specific land use composition of contributing watersheds for the various study results. In some
cases, the monitoring was performed in waterways that include contributions from a variety of
land use types, but in all cases the monitored watershed includes an urban component.
Primary information sources include published scientific literature, as well as unpublished data
produced under the direction of public agencies. All primary information sources are clearly
referenced, including web links where available.
This report provides summaries of the various study results as provided by the study authors.
Where the underlying data or statistical summaries of the data were available, this report also
separately summarizes the chemistry and toxicity testing data. Distinctions are made for data
produced from water vs. sediment matrices, and from urban runoff discharges vs. receiving
waters (i.e., named water bodies that receive urban runoff discharges). The investigation was
limited to surface waters; results of groundwater monitoring are not included.
The Chemistry Results Summary and Toxicity Results Summary tables contain data only for
more recent studies, generally those published during 2008-2012, covering data generated since
ca. 2005. This compilation is as complete as was feasible as of mid-calendar year 2012, but may
not include every relevant study. Ongoing and planned monitoring undoubtedly will continue to
reveal additional evidence of the presence of pyrethroids and other pesticides - and related
effects - in California’s urban watersheds. This work should be updated periodically to
incorporate additional material as it becomes available. This will be particularly important as
other insecticides, beyond fipronil, become more commonly used. The underlying spreadsheets
upon which this report’s tables are based are readily expandable, and can be updated over time.
Notes regarding nomenclature and approach used in this study:
x
Chemical names, rather than brand names, are used to designate the pesticides.
x
Like pyrethrins, pyrethroids have multiple chiral isomers. Most commercial products are
comprised of mixtures of these isomers (e.g., permethrin is generally available as a
mixture of cis-permethrin and trans-permethrin). Only a few pyrethroids appear as single
isomers in commercial products (e.g., esfenvalerate, beta-cyfluthrin). Although it is
known that chirality can affect toxicity (Gerlach, 2012), not enough information is
available to adequately assess this factor in the context of the current report, in part
because most laboratories do not report results on an isomer-specific basis. For purposes
of this summary, where isomer-specific data are available, these have been totaled by
chemical (e.g., “permethrin” includes the sum of available data for cis-permethrin and
trans-permethrin).
Page 5 x
The summary tables generally exclude studies that relied on chemical analysis methods
that are incapable of detecting pyrethroids at the ng/L (water) or ng/g (sediment)
concentration levels, as non-detect results at higher analytical detection levels do not
indicate whether potentially harmful concentrations of pyrethroids are actually present.
Findings
There is an expanding diversity of research focusing on the presence and effects of pesticides in
the environment within California. Earlier (pre-2000) research on pesticides effects focused
principally on agricultural areas, but that has changed in recent years. Many studies are now
available documenting the presence and effects of pyrethroids and other pesticides in urban
areas. Over 100 studies were evaluated for this project. After eliminating reports presenting
repeat data, purely methods research projects, and studies involving predominantly agricultural
watersheds, summaries are provided for over 80 studies. Many more projects and studies are
currently being undertaken or planned. Over 9200 pyrethroid sample analysis results and over
3200 results for fipronil and degradates were evaluated and summarized for this report.
Summary of Findings – Pyrethroid Pesticides
Pyrethroids are frequently detected at quantifiable levels in both water and sediment in urban
waterways throughout California. For environmental contaminants such as pesticides, the rate of
analytical (laboratory) detection is an important metric, as it indicates how frequently the
pesticide is observed at a quantifiable level in environmental samples. Due to the very low
concentrations at which many of these pesticides can cause toxicity, the rate of detection is a
useful indicator of the extent to which these chemicals are migrating from the site of application
to the aquatic environment. The rates of analytical detection from the summarized chemistry
results are presented in Table 3 for the most commonly-detected pyrethroids. This table generally
summarizes chemistry data for the more recent studies evaluated (those published since 2005).
Because detection rates are only relevant for studies that employ environmentally relevant
detection limits, this summary focuses on studies that reported chemical analysis methods
capable of detecting pyrethroids at the ng/L (water) or ng/g (sediment) concentration levels.
Results are shown separately for water and sediment samples.
Bifenthrin, considered to be the leading cause of pyrethroid-related toxicity in urban areas (c.f.,
Weston et al., 2005; Amweg et al., 2006; Holmes et al., 2008, TDC Environmental, 2006), was
detected most frequently of all the pesticides evaluated, in both water and sediment. For samples
tested in studies evaluated for this summary, the rate of analytical detection for bifenthrin was
69% in sediment samples and 64% in water samples, as indicated in Table 3.
Detection rates were generally higher for pyrethroids in sediment than in water. Permethrin was
the most extreme case of this difference, detected in 50% of sediment samples but only 16% of
water samples. Overall, pyrethroids were detected at a rate of 31% in sediments and 24% in
water samples.
Page 6 Table 3. Analytical Detection Rates – Pyrethroids
WATER SAMPLES:
Allethrin
Bifenthrin
Cyfluthrin
Cyhalothrin
Cypermethrin
Deltamethrin/Tralomethrin
Esfenvalerate/Fenvalerate
Fenpropathrin
Fluvalinate
Permethrin
Phenothrin
Prallethrin
Resmethrin
Tetramethrin
All Pyrethroids
#
%
Samples Detected
235
0.4%
748
64%
847
28%
663
22%
503
31%
533
5%
704
19%
306
21%
224
3%
1,146
16%
5
0%
219
2%
175
0%
16
6%
6,511
24%
SEDIMENT SAMPLES:
Allethrin
Bifenthrin
Cyfluthrin
Cyhalothrin
Cypermethrin
Fenpropathrin
Fluvalinate
Permethrin
Phenothrin
Prallethrin
Resmethrin
Tetramethrin
All Pyrethroids
#
%
Samples Detected
64
0%
359
69%
324
33%
334
30%
284
29%
252
22%
314
12%
147
16%
59
3%
367
50%
8
13%
46
0%
117
3%
23
0%
2,704
31%
Notes for Table 3:
Table summarizes data for more recent studies evaluated (generally published since 2005).
This summary generally includes only data from studies that relied on chemical analysis methods
capable of detecting pyrethroids at the ng/L (water) or ng/g (sediment) concentration levels.
Fenpropathrin (trade name, Danitol) has no registered urban uses; the levels of detection may reflect
results from mixed-use watersheds and/or drift from agricultural areas to urban watersheds.
Page 7 Pyrethroid Concentrations – Water
Pyrethroids were commonly found at concentrations exceeding levels known to cause toxicity to
aquatic organisms in water. The average and maximum concentrations from the summarized
water chemistry results are presented in Table 4 for the pyrethroids, along with the relevant acute
and chronic aquatic toxicity comparison values from Table 1. This table generally summarizes
chemistry data for the more recent studies evaluated (those published since 2005).
For all five pyrethroids for which there are UC Davis chronic toxicity criteria comparison values
in Table 1, the average observed environmental concentration is higher than the chronic toxicity
comparison value. The average reported concentrations of bifenthrin, cyfluthrin, cyhalothrin,
cypermethrin and permethrin in water samples range from approximately one to more than three
orders of magnitude above the chronic criteria values published by UC Davis (from Table 1).
Maximum reported concentrations of these five pyrethroids are in the range of two to more than
four orders of magnitude higher than the UC Davis acute criteria values (from Table 1). The
most prominent examples from Table 4 include:
x The maximum reported concentration of bifenthrin in water was 398 ng/L, compared to
the UC Davis acute criterion value of 4 ng/L;
x The maximum reported concentration of cypermethrin in water was 519 ng/L, compared
to the UC Davis acute criterion value of 1 ng/L;
x The maximum reported concentration of permethrin in water was 12,652 ng/L, compared
to the UC Davis acute criterion value of 10 ng/L.
Pyrethroid Concentrations – Sediment
The average and maximum concentrations from the summarized sediment chemistry results are
presented in Table 5 for the pyrethroids. Published LC50 values exist for Hyalella azteca
exposure in sediments for several pyrethroids (Amweg, et al., 2005; Maund et al., 2002).
However, because organic carbon helps mitigate pyrethroid toxicity to invertebrates in
sediments, these LC50 values are expressed as µg/g organic carbon. Conversion of the statewide
sediment data to the organic carbon-normalized format was beyond the scope of this report (and
not all sources provide organic carbon data). Nonetheless, for the seven pyrethroids for which
sediment LC50 values are available, it is apparent that the average concentrations reported in
Table 5 would be substantially greater than the published LC50s following organic carbon
normalization, assuming a typical organic carbon level of 1-3 percent for California sediments
(c.f., Amweg et al., 2005). This means that, under average conditions in urban waterways in
California, these pesticides are typically present at levels toxic to sensitive macroinvertebrates
such as Hyalella azteca in sediments. As shown in Table 5, the level of exceedance of the
average reported concentration over the LC50 value is particularly significant for bifenthrin.
Multiple Pyrethroids Commonly Detected
Multiple pyrethroids typically were found in each sample in the summarized chemistry studies,
in both water and sediment samples. Because pyrethroid toxicity is generally considered to be
additive (c.f., Trimble et al., 2009), the actual in-situ toxicity estimated from chemistry results
must account for the mixtures of pyrethroids and other pesticides found.
Page 8 Table 4. Average and Maximum Reported Pyrethroid Concentrations (Water) Compared to U.C. Davis Criteria Values
WATER SAMPLES:
Allethrin
Bifenthrin
Cyfluthrin
Cyhalothrin
Cypermethrin
Fenpropathrin
Fluvalinate
Permethrin
Phenothrin
Prallethrin
Resmethrin
Tetramethrin
Average
Conc.
(ppt)
0.203
26
14.9
4.80
13.3
1.40
1.43
4.80
0.566
51.2
ND
2.13
ND
0.219
Maximum
Conc.
(ppt)
9.50
398
423
243
519
252
36.8
459.9
154.8
12652
ND
287
ND
2.80
UC Davis
Chronic
Criterion
Value
(ppt)
Ratio of
Average
Conc.:
Chronic
Criterion
Value
UC Davis
Acute
Criterion
Value
(ppt)
Ratio of
Maximum
Conc.:
Acute
Criterion
Value
0.6
0.05
0.5
0.2
43
298
10
66
4
0.3
1
1
100
1409
243
519
2
26
10
1265
Notes for Table 4:
“Average” concentrations = mean values of mean concentrations reported from summarized studies.
“ppt” = parts per trillion
“ND” means all data were reported as non-detect.
Water column toxicity criteria comparison values shown are the UC Davis chronic and acute criteria; see Table 1 for references.
Fenpropathrin has no registered urban uses; the reported concentrations may reflect results from mixed-use watersheds and/or drift from
agricultural areas to urban watersheds.
Page 9 Table 5. Average and Maximum Reported Sediment Concentrations – Pyrethroids
SEDIMENT SAMPLES:
Allethrin
Bifenthrin
Cyfluthrin
Cyhalothrin
Cypermethrin
Fenpropathrin
Fluvalinate
Permethrin
Phenothrin
Prallethrin
Resmethrin
Tetramethrin
Average
Conc.
(ppb)
ND
45.8
17.4
4.64
10.1
5.11
1.47
0.393
0.080
27.8
0.661
ND
2.03
ND
Max.
Conc.
(ppb)
ND
744
187
31.9
987.5
78.0
20.3
8.8
3.60
539
0.750
ND
24.0
ND
Published
LC50
Values
(µg/g organic carbon)
0.52
1.08
0.45
0.79
1.54
10.83
Notes for Table 5:
“ND” means all data were reported as non-detect.
“ppb” = parts per billion
Published LC50 Values (Amweg et al., 2005; Maund et al., 2002) are reported as organic carbonnormalized values (µg/g organic carbon), calculated by dividing the measured pyrethroid
concentration by the measured percent organic carbon in the sediment sample. The organic carbonnormalized LC50 values therefore cannot be directly compared to the average or maximum observed
concentrations for pyrethroids in sediments. The organic carbon-normalized average and maximum
pyrethroid concentrations would be higher than those shown by a factor of roughly 33-100, assuming
typical sediment organic carbon concentrations of 1-3%.
Fenpropathrin has no registered urban uses; the reported concentrations may reflect results from
mixed-use watersheds and/or drift from agricultural areas to urban watersheds.
Page 10 Summary of Findings – Fipronil and Degradates
The non-pyrethroid pesticide, fipronil, is a leading replacement for pyrethroid pesticides in urban
areas (TDC Environmental, 2007). Fipronil has multiple degradates, some of which are more
environmentally stable than fipronil itself, and some of which have equal or greater aquatic
toxicity than the parent compound. Fipronil and its degradates also are frequently detected in
both water and sediment in urban watercourses. Data were identified for Fipronil Amide,
Fipronil Desulfinyl, Fipronil Desulfinyl Amide, Fipronil Sulfide, and Fipronil Sulfone. The rates
of analytical detection from the summarized chemistry results are presented in Table 6 for
fipronil and its degradates. Results are shown for both water and sediment samples.
Fipronil was detected in 39% of water samples tested from studies evaluated for this summary,
and 19% of sediment samples. This is in contrast to the pattern for most pyrethroids, for which
there were typically higher percent detections in sediment. Presumably this reflects fipronil’s
lower KOW, and/or fipronil’s relatively higher solubility in water.
The fipronil degradates as a group were detected analytically in 24% of the water samples tested
from studies evaluated for this study, and 35% of sediment samples. This pattern is similar to
that of the pyrethroids.
Table 6.
Analytical Detection Rates – Fipronil and Degradates
WATER SAMPLES:
Fipronil
Fipronil degradates
#
%
Samples Detected
871
39%
2,271
24%
SEDIMENT SAMPLES:
Fipronil
Fipronil degradates
#
%
Samples Detected
16
19%
48
35%
Notes for Table 6:
“Fipronil degradates” included are: Fipronil Amide, Fipronil Desulfinyl, Fipronil Desulfinyl Amide,
Fipronil Sulfide, and Fipronil Sulfone.
The average and maximum concentrations from the summarized chemistry results are presented
in Table 7 for fipronil and the group of fipronil degradates. As shown in Table 2, some published
aquatic toxicity values and all of the published USEPA benchmarks for fipronil and its principal
degradates are in the sub-ppb (µg/L) range. Average fipronil concentrations in water samples
were higher than the USEPA Aquatic Life Benchmark for fipronil, while average concentrations
of the fipronil degradates were in the range of the associated USEPA benchmarks, as shown in
Table 7. The maximum reported concentrations for fipronil and its degradates in water samples
were well above the USEPA benchmarks. Similarly, the maximum reported concentrations of
fipronil and its degradates in sediment samples were well above published LC50 values.
Page 11 Table 7. Average and Maximum Reported Concentrations in Water and Sediment –
Fipronil and Degradates
WATER SAMPLES:
Fipronil
Fipronil degradates
SEDIMENT
SAMPLES:
Fipronil
Fipronil degradates
Average
Conc.
(ppt)
89.7
71.2
Average
Conc.
(ppb)
0.078
0.297
Max.
Conc.
(ppt)
10004
1961
US EPA
Aquatic
Life
Benchmark
(ppt)
11
37-590
Max.
Conc.
(ppb)
0.30
2.60
Published
LC50
Values
(µg/g organic carbon)
0.13
0.12-0.16
Notes for Table 7:
Water sample results are reported as ppt (parts per trillion), while sediment results are reported as ppb
(parts per billion).
“Fipronil degradates” included are: Fipronil Amide, Fipronil Desulfinyl, Fipronil Desulfinyl Amide,
Fipronil Sulfide, and Fipronil Sulfone.
Published sediment LC50 Values (Maul et al., 2008) are reported as organic carbon-normalized values
(µg/g organic carbon), calculated by dividing the measured pyrethroid concentration by the measured
percent organic carbon in the sediment sample. The organic carbon-normalized LC50 values therefore
cannot be directly compared to the average or maximum observed concentrations for pyrethroids in
sediments. The organic carbon-normalized average and maximum fipronil concentrations would be
higher than those shown by a factor of roughly 33-100, assuming typical sediment organic carbon
concentrations of 1-3%.
Summary of Findings – Toxicity
Toxic effects are documented in both water and sediment in urban waterways throughout
California. Effects of pyrethroids on aquatic organisms are widespread throughout the aquatic
environment, as documented in studies involving water column toxicity testing, sediment
toxicity testing, and tissue analysis. Of the 25 toxicity studies that were summarized, all reported
some level of toxicity for one or more organisms tested.
There has been a notable shift in aquatic (water column) toxicity in urban areas since the phaseout of urban uses of diazinon and chlorpyrifos in the early 2000s. Prior to that time, samples of
urban runoff and urban creeks were frequently found to be toxic to Ceriodaphnia, with the
organophosphate pesticides diazinon and chlorpyrifos commonly identified as the likely causes
(c.f., San Francisco Bay Regional Quality Control Board, 2005; Anderson et al., 2011). Since the
federally mandated restrictions in diazinon and chlorpyrifos took effect, there have been few
Page 12 reports of toxicity to Ceriodaphnia, from samples collected in urban (non-agricultural) waters,
and few reports of toxicity due to the organophosphate pesticides.
The common amphipod, Hyalella azteca, is more sensitive to pyrethroid pesticides than other
common test species (Amweg et al., 2005; Anderson et al., 2011). Data reviewed for this report
show that urban waters in recent years frequently have exhibited toxicity to Hyalella azteca, with
pyrethroids as the likely cause, based on TIEs and correlations with pyrethroid chemical
concentration data (see also a summary in Anderson et al., 2011).
Early research into the toxic effects of pyrethroids as replacement pesticides for the
organophosphate pesticides indicated widespread sediment toxicity in urban areas of California
(c.f., Amweg et al., 2005, Amweg et al. 2006, Holmes et al., 2008, Weston et al. 2005). In these
studies, pyrethroids were identified as the apparent cause of the sediment toxicity.
While the toxic effects of pyrethroids in sediments have now been thoroughly documented,
recent research also highlights the toxic effects of pyrethroids in water column samples. For
example, Weston and Lydy (2012) found that water samples from five of seven creeks tested
during a 2009 rain event were toxic to Hyalella, with acute toxicity (mortality or paralysis) rates
in the toxic samples ranging from 74% to 96%. Over half (52%) of water samples from two
stations in the lower American River collected during storm events in 2009-2010 were acutely
toxic to Hyalella. TIEs and water chemistry testing were used to identify pyrethroids as the cause
of most of the observed water column toxicity.
The results of a number of the toxicity studies that are summarized in this report were further
evaluated in a 2011 SWAMP report entitled, Toxicity in California Waters (Anderson et al,
2011). The reader is referred to that report for additional information on state-sponsored toxicity
studies conducted during the period 2001-2010. The period of the SWAMP review spans the
transition from the phase-out of orthophosphate pesticides to the rise in prominence of
pyrethroids as replacement pesticides. The study includes discussions of comparisons of toxicity
test results among urban, agricultural, and open space locations, as well as the findings from
toxicity identification studies (TIEs) linking specific pesticides to toxicity.
Geographical Summary
Lists of the water bodies for which data were summarized are shown in Table 8a (Northern and
Central California) and Table 8b (Southern California), and then alphabetically by water body
name within each of those two regions.
Evidence of the presence and effects of pyrethroids and fipronil, and associated toxic effects in
urban watercourses, is widely distributed geographically throughout the state of California. The
review identified data from the North Coast, Lake Tahoe region, San Francisco Bay Area,
Central Valley, Central Coast, and both coastal and inland areas of Southern California.
Pyrethroid-related toxicity has been documented in nearly every major urban watershed in the
state and eight of the nine California Water Board regions.
Page 13 Table 8a.
Northern/Central California Monitoring Locations with
Reported Chemistry/Toxicity Results
Monitoring Location(s)
Alamo Creek
Alder Creek
Alisal Creek
Geographic Area
Solano County
Sacramento County
Monterey County
American Canyon Creek
American River
Napa County
Sacramento County
Sacramento County
Arcade Creek
Blue Rock Springs
Bodega Bay
Carpinteria Salt Marsh
Castro Valley Creek
Chicken Ranch Slough
Corte Madera Creek
Coyote Creek (fresh)
Coyote Creek (tidal)
Curry Creek
Dry Creek
Ducker Creek
Elder Creek
Elk Grove storm drains
Gabilan Creek
Solano County
Sonoma County
Santa Barbara County
Alameda County
Sacramento County
Marin County
Santa Clara County
Santa Clara County
Sarasota County
Roseville
Sonoma County
Sacramento County
Sacramento County
Monterey County
Glen Echo Creek
Grayson Creek
Alameda County
Contra Costa County
Hinebaugh Creek
Hospital Creek
Ingram Creek
Sonoma County
San Joaquin County.
San Joaquin County.
Jane's Creek Meadows
Kaseberg Creek
Kirker Creek
Koopman Canyon Creek
Laguna Creek
Humboldt County
Roseville
Contra Costa County
Alameda County
Sacramento County
Lauterwasser Creek
Lion Creek
Mammoth Creek
Marsh Creek
Martin Canyon Creek
Merced River
Contra Costa County
City of Oakland
Tahoe/Lahontan Area
Contra Costa County
Alameda County
Merced County
Napa River (fresh)
Napa County
Page 14 Water
Board
Region
5
5
3
2
5
5
2
1
3
2
5
2
2
2
5
5
1
5
5
3
2
2
1
5
5
1
5
2
2
5
2
2
6
5
2
5
2
Napa River (tidal)
Natividad Creek
Natomas drain
Napa County
Monterey County
Sacramento County
Petaluma River (fresh)
Petaluma River (tidal)
Pine Creek
Pleasant Grove Creek
Sonoma County
Marin County
Contra Costa County
Placer County
Quimby Creek
Rheem Creek
Roseville storm drains
Sacramento River
Sacramento-San Joaquin Delta
Santa Clara County
Contra Costa County
Placer County
Sacramento County
Sacramento County
Salinas urban creeks
San Francisquito Creek
San Joaquin River
San Joaquin River tributaries
Salinas
San Mateo/Santa Clara Counties
San Joaquin R. Valley
San Joaquin R. Valley
San Leandro Creek
San Lorenzo Creek
San Mateo Creek
San Pablo Creek
South Branch
Stanislaus Creek
Stege Marsh
Alameda County
San Leandro
San Mateo County
Contra Costa County
Roseville
Stanislaus County
Contra Costa County
Stevens Creek
Stockton Creek
Strong Ranch Slough
Santa Clara County
Sacramento County
Sacramento County
Suburban watershed
Suisun Slough Tributary
Sump 111
Bodega Bay
Solano County
Sacramento County
Tahoe Keys
Truckee River Swale
Tuolumne Creek
Ulatis Creek
Tahoe/Lahontan Area
Tahoe/Lahontan Area
Stanislaus County
Solano County
Willow Creek
Sacramento County
Page 15 2
3
5
2
2
2
5
2
2
5
5
5
3
2
5
5
2
2
2
2
5
5
2
2
5
5
1
2
5
6
6
5
5
5
Table 8b.
Southern California Monitoring Locations with
Reported Chemistry/Toxicity Results
Bouquet Canyon Creek
Calleguas Creek
Los Angeles County
Los Angeles County
Los Angeles County
Los Angeles County
Ventura County
Cole Creek
Chollas Creek
Chollas Creek - North Fork
Chollas Creek - South Fork
Riverside County
San Diego County
San Diego County
San Diego County
Conejo Creek
Cottonwood Creek
Huntington Harbor tributaries
Los Angeles River
Lindo Lake
Calleguas Creek Watershed
San Diego County
Long Canyon Channel
Los Peñasquitos Creek
Mugu Lagoon
Murrieta Creek
N. Fork Arroyo Conejo
New River at Boundary
Newport Harbor
Newport Harbor tributaries
Peters Canyon Wash
Revolon Slough
Redhawk Channel
Salt Creek watershed
San Diego River
San Diego Harbor
Riverside County
San Diego County
San Dieguito River
San Juan Creek
San Luis Rey River
Santa Gertrudis Channel
San Marcos Creek
Santa Clara River watershed
San Diego County
Orange County
San Diego County
Riverside County
San Diego County
Ventura County
Santa Margarita River
Santa Margarita R.
tributaries
Riverside County
Water
Board
Region
9
4
4
4
4 4
8
9
9
9
4
9
8
4
9
8
9
4
9
4
9
8
8
8
4
8
8
9
9
9
9
9
8
9
4
9
Riverside County
9
Agua Hedionda Creek
Arroyo Seco Channel
Ballona Creek
Ballona Creek Estuary
Geographic Area
San Diego County
Huntington Harbor/Orange County
Los Angeles County
San Diego County
Ventura County
Riverside County
Calexico
Orange County
Orange County
Orange County
Riverside County
Orange County
San Diego County
San Diego County
Page 16 Sweetwater River
Switzer Creek
Tecolote Creek
Temecula Creek
Tijuana River
Upper Newport Bay
Warm Springs Channel
Wood Creek watershed
San Diego County
City of San Diego
City of San Diego
Riverside County
San Diego County
Newport Bay
Riverside County
Orange County
Page 17 9
9
9
9
9
8
8
8
Detailed Results
Details of the summarized studies are presented in the tables included in the appendices, as
described below. These appendix tables are based on spreadsheets in which information can be
easily sorted and from which selected information can be extracted, and there are a number of
clickable web links to studies.
The appendices to this memorandum include the following tables:
Appendix A: The “Study Summaries by Author” table, organized alphabetically by abbreviated
citation in (author, date) format. This table contains detailed information on the source
documents, including web links where available (in some cases these links lead to just an
abstract or perhaps ordering information). The "Citation – Abbrev." field can be used as a
cross-reference for the various studies across the different tables.
Appendix B: The “Results Summaries by Geography” table contains at-a-glance summaries of
the methods and key results of the compiled studies. The Results Summaries entries are
organized geographically (Northern/Central California vs. Southern California and then by
local area, nominally ordered from north to south within each of those two regions).
Appendix C: The “Chemistry Results Summary” table contains detailed results of water and
sediment chemistry tests compiled where available from the more recent studies (generally
those published 2005-2012) summarized in the preceding tables. The Chemistry Results
Summary table summarizes results for more than 12,400 pesticide analyses (including
pyrethroid pesticides plus fipronil and its degradates).
Appendix D: The “Toxicity Results Summary” table contains detailed results of water and
sediment toxicity tests compiled where available from the more recent studies (generally
those published 2005-2012) summarized in the preceding tables.
Note that the Study Summaries by Author (Appendix A) and Results Summaries by Geography
(Appendix B) tables contain all studies investigated and found to be pertinent, including the
studies evaluated for the previous (2008) Pyrethroids Data Compilation. The Chemistry Results
Summary (Appendix C) and Toxicity Results Summary (Appendix D) tables contain data only
for more recent studies evaluated for the current report, generally those published since 2005.
Page 18 Recommendations
Improvements in Laboratory Analytical Methods Are Needed
Some studies involving chemical analysis of pyrethroids in water and sediment are performed
with analytical detection limits that are not sufficiently low to detect these pesticides at
environmentally relevant concentrations. This has the effect of understating the extent of the
problem, as some samples reported as “non-detect” may in fact contain pyrethroids at potentially
harmful concentrations. Personnel responsible for pesticides analysis should ensure that the
analytical work can be done so as to detect the target pesticides at environmentally relevant
concentrations (i.e., near the “comparison values” shown in Tables 1 and 2). Some commercial
laboratories are currently capable of providing appropriate analytical detection limits on a routine
basis. However, a systematic means is called for by which analytical protocols are established at
the federal level, with analytical detection limits sufficient to detect pesticides at
environmentally-relevant concentrations in both waters and sediments.
Cumulative Impacts of Pesticide Mixtures Should Be Addressed
A clear need exists for quantitative assessment of cumulative impacts of pesticide mixtures, as
this appears to be a significant factor contributing to the observed toxicity in urban creeks.
Conclusions
Monitoring data compiled for this report indicate significant levels of pyrethroid pesticides found
in water and sediment samples from surface waters in California’s urban areas. Average reported
concentrations of several commonly-used pyrethroids in urban water samples are typically well
above published comparison values, including UC Davis chronic toxicity criteria levels and
USEPA Aquatic Life Benchmarks. Under average conditions in the sediments of urban
waterways in California, pyrethroids also are typically present at levels known to be toxic to
sensitive organisms. Bifenthrin, thought to be a principal cause of toxicity in urban waterways, is
found in 64% of water samples and 67% of sediment samples in urban areas of California.
Detections of pyrethroid pesticides in both water and sediment are widely distributed
geographically throughout the state. In most samples, multiple pyrethroids are detected.
Fipronil, a common pyrethroid replacement pesticide, is also found in substantial numbers of
water and sediment samples, along with its most common degradate compounds. Average
fipronil concentrations in water samples are higher than the USEPA Aquatic Life Benchmark for
fipronil, while average concentrations of the fipronil degradates are in the range of the associated
USEPA benchmarks. The maximum reported concentrations for fipronil and its degradates in
water samples are well above the USEPA benchmarks. Similarly, the maximum reported
concentrations of fipronil and its degradates in sediment samples are well above published
toxicity (LC50) values.
Toxicity in urban waterways throughout California is also well-documented in the compiled
results, with many studies indicating pyrethroids as the likely cause of the observed toxicity.
Because pyrethroid toxicity is generally considered to be additive, the level of toxicity estimated
from chemistry results must account for the mixtures of pyrethroids and other pesticides found,
including fipronil.
Page 19 References
Amweg, E. L., D. P. Weston, and N. Ureda (2005). “Use and Toxicity of Pyrethroid Pesticides in
the Central Valley, California, USA.” Environ. Tox. Chem., 24 (4) 966-972; erratum: 24(5)
Amweg, E. L., D. P. Weston, J. You, M. J. Lydy. (2006). "Pyrethroid Insecticides and Sediment
Toxicity in Urban Creeks from California and Tennessee." Environ. Sci. Technol. 40(5) 17001706.
Anderson, B. S.; Phillips, B. M.; Hunt, J. W.; Connor, V.; Richard, N.; Tjeerdema, R. S. (2006).
Identifying primary stressors impacting macroinvertebrates in the Salinas River (California,
USA): Relative effects of pesticides and suspended particles. Environ. Pollut. 141, 402–408.
Anderson B., Hunt, J., Markiewicz, D., and Larsen, K. (2011). Toxicity in California Waters.
Surface Water Ambient Monitoring Program. California State Water Resources Control Board.
Sacramento, CA." Oct. 2011
Brander, S.M.; Fojut, T.L.; Palumbo, A.J. and Tjeerdema, R.S. (2010). “Water Quality Criteria
Report for Bifenthrin.” Department of Environmental Toxicology, University of California,
Davis, prepared for: California Environmental Protection Agency, Central Valley Regional
Water Quality Control Board. March. Available at:
http://www.swrcb.ca.gov/rwqcb5/water_issues/tmdl/central_valley_projects/central_valley_pesti
cides/criteria_method/bifenthrin/final_bifenthrin_criteria_rpt.pdf
Central Valley RWQCB. (2006). Sacramento and San Joaquin River Watersheds Pesticide Basin
Plan Amendment Fact Sheet. California Regional Water Quality Control Board, Central Valley
Region. October. Available at:
cides/att2_fact.pdf
Fojut, T.L.; Chang, S. and Tjeerdema, R.S. (2010). “Water Quality Criteria Report for
Cyfluthrin.” Department of Environmental Toxicology, University of California, Davis, prepared
for the California Environmental Protection Agency, Central Valley Regional Water Quality
Control Board. March. Available at:
cides/criteria_method/cyfluthrin/final_cyfluthrin_criteria_rpt.pdf
Fojut, T.L. and Tjeerdema, R.S. (2010). “Water Quality Criteria Report for LambdaCyhalothrin.” Department of Environmental Toxicology, University of California, Davis,
prepared for: California Environmental Protection Agency, Central Valley Regional Water
Quality Control Board. March. Available at:
cides/criteria_method/lambda_cyhalothrin/final_lambda_cyhalothrin_criteria_rpt.pdf
Fojut, T.L.; Mulligan, R. and Tjeerdema, R.S. (2011a). “Water Quality Criteria Report for
Cypermethrin.” Department of Environmental Toxicology, University of California, Davis,
Quality Control Board. September. Available at:
Page 20 http://www.swrcb.ca.gov/rwqcb5/water_issues/tmdl/central_valley_projects/central_valley_pesti
cides/criteria_method/cypermethrin/cypermethrin_final_criteria.pdf
Fojut, T.L.; Rering, C. and Tjeerdema, R.S. (2011b). “Water Quality Criteria Report for
Permethrin.” Department of Environmental Toxicology, University of California, Davis,
Quality Control Board. September. Available at:
cides/criteria_method/permethrin/permethrin_final_criteria.pdf Gerlach, R.W. (2012). Chiral Chemistry and Toxicity Assessments for Pyrethroid Pesticides, in
Parameters for Pesticide QSAR and PBPK/PD Models for Human Risk Assessment, Chapter 2,
pp 19–29, ACS Symposium Series, Vol. 1099
Gunasekara, A. S. and T. Troung (2007). “Environmental Fate of Fipronil.” Environmental
Monitoring Branch, Department of Pesticide Regulation, California Environmental Protection
Agency, Sacramento, CA. Revised March 5, 2007
Holmes, R. W., B. S. Anderson, et al. (2008). "Statewide investigation of the role of pyrethroid
pesticides in sediment toxicity in California's urban waterways." Environmental Science and
Technology 42(18): 7003-9.
Konwick, B.J., A.T. Fisk, et al. (2005). "Acute Enantioselective Toxicity of Fipronil and Its
Desulfinyl Photoproduct to Ceriodaphnia Dubia." Environmental Toxicology and Chemistry
24(9): 2350-2355; supplemented by addendum with corrected citations for aquatic toxicity data
Environ. Toxicol. Chem. 25(4): 1184.
Maul, J.D., A.A. Brennan, A.D. Harwood, and M.J. Lydy. (2008). Effect of sediment-associated
pyrethroids, fipronil, and metabolites on Chironomus tentans growth rate, body mass, condition
index, immobilization, and survival. Environ. Toxicol. Chem. 27 (12): 2582–2590.
Maund, S. J., Hamer, M. J., Warinton, J. S. and Kedwards, T. J. (1998). Aquatic ecotoxicology
of the pyrethroid insecticide lambda-cyhalothrin: considerations for higher-tier aquatic risk
assessment. Pestic. Sci., 54: 408–417. doi: 10.1002/(SICI)1096-9063(199812)54:4<408::AIDPS843>3.0.CO;2-T
Maund, S. J.; Hamer, M. J.; Lane, M. C. G.; Farrelly, E.; Rapley, J. H.; Goggin, U. M.; Gentle,
W. E. (2002). Partitioning, bioavailability, and toxicity of the pyrethroid insecticide
cypermethrin in sediments. Environ. Toxicol. Chem. 21: 9-15.
Mize, S.V.; S.D. Porter, and D.K. Demcheck (2008). "Influence of fipronil compounds and ricecultivation land-use intensity on macroinvertebrate communities in streams of southwestern
Louisiana, USA". USGS Staff -- Published Research. Paper 435.
Mokry, L. E. and Hoagland, K. D. (1990). Acute toxicities of five synthetic pyrethroid
insecticides to Daphnia magna and Ceriodaphnia dubia. Environmental Toxicology and
Chemistry, 9: 1045–1051. doi: 10.1002/etc.5620090811
Moran, K.D., and P.L. TenBrook (2011). “Sources of Pyrethroid Insecticides in California’s
Urban Watersheds: A Conceptual Model.” In Pesticide Mitigation Strategies for Surface Water
Page 21 Quality; Goh, K.S., J. Gan, and B. Bret, Eds. ACS Symposium Series; American Chemical
Society: Washington, DC.
Ruby, A. (2008). “Pyrethroids Monitoring Data Compilation”. Memorandum prepared for the
California Stormwater Quality Association (CASQA) by Armand Ruby Consulting. July 8.
San Francisco Bay Regional Quality Control Board (2005). Diazinon and Pesticide-Related
Toxicity in Bay Area Urban Creeks Water Quality Attainment Strategy and Total Maximum
Daily Load (TMDL), Proposed Basin Plan Amendment and Staff Report. California Regional
Water Quality Control Board, San Francisco Bay Region. November 9, 2005. Available at:
http://www.waterboards.ca.gov/sanfranciscobay/water_issues/programs/TMDLs/urbancrksdiazinon/b_final_staff_report.pdf
State Water Resources Control Board (2011). Impaired Water Bodies web site; see:
http://www.swrcb.ca.gov/water_issues/programs/tmdl/integrated2010.shtml
TDC Environmental (2006). Pesticides in Urban Surface Water: Annual Research and
Monitoring Update 2006. Prepared for the San Francisco Estuary Project. April.
TDC Environmental (2007). Urban Use of the Insecticide Fipronil--Water Quality Implications,
Memorandum to the Urban Pesticide Committee from Kelly D. Moran, June 18, 2007.
TDC Environmental (2010a). Pesticides in Urban Runoff, Wastewater, and Surface Water:
Annual Review of New Scientific Findings 2010. Prepared for the San Francisco Estuary
Partnership. March.
TDC Environmental (2010b). Pesticides in Urban Runoff, Wastewater, and Surface Water:
Annual Urban Pesticide Use Data Report 2010. Prepared for the San Francisco Estuary
Partnership. June.
Trimble, A. J., D. P. Weston, J. B. Belden, M. J. Lydy. (2009). "Identification and Evaluation of
Pyrethroid Insecticide Mixtures in Urban Sediments." Environmental Toxicology and Chemistry
28(8): 1687-1695.
UC Davis criteria development reports (Brander et al., 2010; Fojut et al., 2010; Fojut and
Tjeerdema, 2010; Fojut et al., 2011a; Fojut et al., 2011b) are available on the Central Valley
Regional Water Quality Control Board website: http://tinyurl.com/2etvvg3
U.S. EPA Aquatic Life Benchmarks website:
http://www.epa.gov/oppefed1/ecorisk_ders/aquatic_life_benchmark.htm
Werner, I. and K. Moran. (2008). Effects of Pyrethroid Insecticides on Aquatic Organisms. In
Synthetic Pyrethroids, Am. Chem. Soc.: Washington, DC, 2008; pp 310-334.
Weston, D. P., R. W. Holmes, J. You, M. J. Lydy. (2005). “Aquatic Toxicity Due to Residential
Use of Pyrethroid Insecticides,” Environ. Sci. Technol. 39(24): 9778-9784.
Weston, D.P. and C.J. Jackson. (2009). Use of Engineered Enzymes to Identify
Organophosphate and Pyrethroid-Related Toxicity in Toxicity Identification Evaluations
Environ. Sci. Technol. 2009, 43, 5514–5520
Page 22 Appendix A:“Study Summaries by Author” Table
Citation - Abbrev.
Author(s)/Date
Agency
Report/Study Title
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Appendix B: “Results Summaries by Geography” Table
Geographic Area
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Citation - Abbrev.
Study Date(s)
Principal Testing Approach
Test Results Summary
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6DQ'LHJR5LYHU6'5
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6DQ'LHJR5LYHU6'5
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Citation - Abbrev.
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
Report/study Title
Region
6DQ'LHJR
6DQ'LHJR
6DQ'LHJR
6DQ'LHJR
2UDQJH&RXQW\
Units
Sed. Unit
Weight
6DQ'LHJR5LYHU6'5
)HQSURSDWKULQ
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6HGLPHQW
5HFHLYLQJ
JNJ
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6DQ'LHJR5LYHU6'5
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6DQ'LHJR5LYHU6'5
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6HGLPHQW
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6DQ'LHJR5LYHU6'5
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6HGLPHQW
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Site(s)
2UDQJH&RXQW\
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Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Mean
Median
'U\
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Min
Max
Notes
6DQ'LHJR5LYHU6'5
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6HGLPHQW
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6DQ'LHJR5LYHU6'5
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Wet/Dry
Weather
6DQ'LHJR5LYHU6'5
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(QVPLQJHUDQG.HOOH\D
Pesticide (Analyte)
6DQ'LHJR5LYHU6'5
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(QVPLQJHUDQG.HOOH\D
Timeframe
3HUPHWKULQFLV
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Citation - Abbrev.
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
Report/study Title
Region
6DFUDPHQWR
6DFUDPHQWR
6DFUDPHQWR
6DFUDPHQWR
Site(s)
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
:RRG&DQ\RQ:&
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
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2WKHUWKUHHVDPSOHYDOXHVPLVVLQJRQO\RQHYDOLGYDOXHUHSRUWHGQRPHDQRUPHGLDQ
Citation - Abbrev.
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
Report/study Title
Region
6DFUDPHQWR
6DFUDPHQWR
6DFUDPHQWR
6DFUDPHQWR
Site(s)
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
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3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
)LSURQLOVXOIRQH
:HW
:DWHU
'LVFKDUJH
%LIHQWKULQ
:HW
:DWHU
'LVFKDUJH
&\IOXWKULQ
:HW
:DWHU
'LVFKDUJH
&\SHUPHWKULQ
:HW
:DWHU
'LVFKDUJH
3HUPHWKULQFLV
:HW
:DWHU
'LVFKDUJH
3HUPHWKULQWUDQV
:HW
:DWHU
'LVFKDUJH
'HVXOILQ\OILSURQLO
'U\
:DWHU
'LVFKDUJH
'HVXOILQ\O)3DPLGH
'U\
:DWHU
)LSURQLO
'U\
)LSURQLODPLGH
'U\
)LSURQLOVXOILGH
)LSURQLOVXOIRQH
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
J/
QJ/
QJ/
QJ/
QJ/
QJ/
J/
'LVFKDUJH
J/
:DWHU
'LVFKDUJH
J/
:DWHU
'LVFKDUJH
J/
'U\
:DWHU
'LVFKDUJH
J/
'U\
:DWHU
'LVFKDUJH
J/
%LIHQWKULQ
'U\
:DWHU
'LVFKDUJH
QJ/
&\IOXWKULQ
'U\
:DWHU
'LVFKDUJH
QJ/
&\SHUPHWKULQ
'U\
:DWHU
'LVFKDUJH
QJ/
2QHVDPSOHYDOXHPLVVLQJ
3HUPHWKULQFLV
'U\
:DWHU
'LVFKDUJH
QJ/
3HUPHWKULQWUDQV
'U\
:DWHU
'LVFKDUJH
QJ/
'HVXOILQ\OILSURQLO
:HW
:DWHU
'LVFKDUJH
J/
'HVXOILQ\O)3DPLGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLO
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLODPLGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOILGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOIRQH
:HW
:DWHU
'LVFKDUJH
J/
%LIHQWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
&\IOXWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
&\SHUPHWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
3HUPHWKULQFLV
:HW
:DWHU
'LVFKDUJH
QJ/
3HUPHWKULQWUDQV
:HW
:DWHU
'LVFKDUJH
QJ/
'HVXOILQ\OILSURQLO
'U\
:DWHU
5HFHLYLQJ
J/
'HVXOILQ\O)3DPLGH
'U\
:DWHU
5HFHLYLQJ
J/
)LSURQLO
'U\
:DWHU
5HFHLYLQJ
J/
)LSURQLODPLGH
'U\
:DWHU
5HFHLYLQJ
J/
)LSURQLOVXOILGH
'U\
:DWHU
5HFHLYLQJ
J/
)LSURQLOVXOIRQH
'U\
:DWHU
5HFHLYLQJ
J/
%LIHQWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
&\IOXWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
&\SHUPHWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
3HUPHWKULQFLV
'U\
:DWHU
5HFHLYLQJ
QJ/
3HUPHWKULQWUDQV
'U\
:DWHU
5HFHLYLQJ
QJ/
'HVXOILQ\OILSURQLO
:HW
:DWHU
5HFHLYLQJ
J/
'HVXOILQ\O)3DPLGH
:HW
:DWHU
5HFHLYLQJ
J/
)LSURQLO
:HW
:DWHU
5HFHLYLQJ
J/
2QHVDPSOHYDOXHPLVVLQJDQG1'VXEVWLWXWHGDVWKHUHSRUWLQJOLPLWJ/
2QHVDPSOHYDOXHPLVVLQJDQG1'VXEVWLWXWHGDVWKHUHSRUWLQJOLPLWJ/
Citation - Abbrev.
Report/study Title
Region
Site(s)
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
3OHDVDQW*URYH&UHHN
3*&
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
6DFUDPHQWR
6DFUDPHQWR
*UD\VRQ&UHHN*5<
(QVPLQJHUDQG.HOOH\D
6DFUDPHQWR
(QVPLQJHUDQG.HOOH\D
6DFUDPHQWR
6DFUDPHQWR
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
)LSURQLODPLGH
:HW
:DWHU
5HFHLYLQJ
J/
)LSURQLOVXOILGH
:HW
:DWHU
5HFHLYLQJ
J/
)LSURQLOVXOIRQH
:HW
:DWHU
5HFHLYLQJ
J/
%LIHQWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
&\IOXWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
&\SHUPHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
3HUPHWKULQFLV
:HW
:DWHU
5HFHLYLQJ
QJ/
3HUPHWKULQWUDQV
:HW
:DWHU
5HFHLYLQJ
QJ/
'HVXOILQ\OILSURQLO
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
'HVXOILQ\O)3DPLGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLO
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLODPLGH
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
)LSURQLOVXOILGH
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
)LSURQLOVXOIRQH
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
%LIHQWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
&\IOXWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
&\SHUPHWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
3HUPHWKULQFLV
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
3HUPHWKULQWUDQV
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
'HVXOILQ\OILSURQLO
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
)LSURQLO
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
)LSURQLODPLGH
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
)LSURQLOVXOILGH
:HW
:DWHU
'LVFKDUJH
J/
'HVXOILQ\O)3DPLGH
:HW
:DWHU
'LVFKDUJH
Sed. Unit
Weight
Mean
Median
Min
Max
1'VXEVWLWXWHGDVWKH5/QJ/
)LSURQLOVXOIRQH
:HW
:DWHU
'LVFKDUJH
J/
%LIHQWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
&\IOXWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
&\SHUPHWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
3HUPHWKULQFLV
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
3HUPHWKULQWUDQV
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
'HVXOILQ\OILSURQLO
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
'HVXOILQ\O)3DPLGH
:HW
:DWHU
'LVFKDUJH
J/
*UD\VRQ&UHHN*5<
)LSURQLO
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLODPLGH
:HW
:DWHU
'LVFKDUJH
)LSURQLOVXOILGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOIRQH
:HW
:DWHU
'LVFKDUJH
J/
%LIHQWKULQ
:HW
:DWHU
'LVFKDUJH
2QHVDPSOHYDOXHPLVVLQJDQG1'VXEVWLWXWHGDVWKH5/QJ/
J/
*UD\VRQ&UHHN*5<
*UD\VRQ&UHHN*5<
J/
*UD\VRQ&UHHN*5<
Notes
*UD\VRQ&UHHN*5<
*UD\VRQ&UHHN*5<
Wet/Dry
Weather
*UD\VRQ&UHHN*5<
*UD\VRQ&UHHN*5<
(QVPLQJHUDQG.HOOH\D
Pesticide (Analyte)
*UD\VRQ&UHHN*5<
*UD\VRQ&UHHN*5<
Timeframe
*UD\VRQ&UHHN*5<
&\IOXWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
&\SHUPHWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
QJ/
*UD\VRQ&UHHN*5<
3HUPHWKULQFLV
:HW
:DWHU
'LVFKDUJH
QJ/
*UD\VRQ&UHHN*5<
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
3HUPHWKULQWUDQV
:HW
:DWHU
'LVFKDUJH
QJ/
'HVXOILQ\OILSURQLO
:HW
:DWHU
'LVFKDUJH
J/
'HVXOILQ\O)3DPLGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLO
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLODPLGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOILGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOIRQH
:HW
:DWHU
'LVFKDUJH
J/
%LIHQWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
&\IOXWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
&\SHUPHWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
3HUPHWKULQFLV
:HW
:DWHU
'LVFKDUJH
QJ/
3HUPHWKULQWUDQV
:HW
:DWHU
'LVFKDUJH
QJ/
'HVXOILQ\OILSURQLO
:HW
:DWHU
'LVFKDUJH
J/
'HVXOILQ\O)3DPLGH
:HW
:DWHU
'LVFKDUJH
J/
Citation - Abbrev.
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
Report/study Title
Region
6DFUDPHQWR
6DFUDPHQWR
2UDQJH&RXQW\
2UDQJH&RXQW\
Site(s)
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
0DUWLQ.RRSPDQ&DQ\RQ
&UHHN0&&
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
)LSURQLO
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLODPLGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOILGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOIRQH
:HW
:DWHU
'LVFKDUJH
J/
%LIHQWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
&\IOXWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
&\SHUPHWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
3HUPHWKULQFLV
:HW
:DWHU
'LVFKDUJH
QJ/
3HUPHWKULQWUDQV
:HW
:DWHU
'LVFKDUJH
QJ/
'HVXOILQ\OILSURQLO
:HW
:DWHU
'LVFKDUJH
J/
'HVXOILQ\O)3DPLGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLO
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLODPLGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOILGH
:HW
:DWHU
'LVFKDUJH
J/
)LSURQLOVXOIRQH
:HW
:DWHU
'LVFKDUJH
J/
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
%LIHQWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
&\IOXWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
&\SHUPHWKULQ
:HW
:DWHU
'LVFKDUJH
QJ/
3HUPHWKULQFLV
:HW
:DWHU
'LVFKDUJH
QJ/
2QHVDPSOHYDOXHPLVVLQJ1'VXEVWLWXWHGDVWKH5/QJ/
3HUPHWKULQWUDQV
:HW
:DWHU
'LVFKDUJH
QJ/
'HVXOILQ\OILSURQLO
:HW
:DWHU
5HFHLYLQJ
J/
'HVXOILQ\O)3DPLGH
:HW
:DWHU
5HFHLYLQJ
J/
)LSURQLO
:HW
:DWHU
5HFHLYLQJ
J/
)LSURQLODPLGH
:HW
:DWHU
5HFHLYLQJ
J/
)LSURQLOVXOILGH
:HW
:DWHU
5HFHLYLQJ
J/
)LSURQLOVXOIRQH
:HW
:DWHU
5HFHLYLQJ
J/
%LIHQWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
&\IOXWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
&\SHUPHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
3HUPHWKULQFLV
:HW
:DWHU
5HFHLYLQJ
QJ/
3HUPHWKULQWUDQV
:HW
:DWHU
5HFHLYLQJ
QJ/
:RRG&DQ\RQ$9
'HVXOILQ\OILSURQLO
'U\
:DWHU
5HFHLYLQJ
J/
J/
2QHVDPSOHYDOXHPLVVLQJ1'VXEVWLWXWHGDVWKH5/QJ/
:RRG&DQ\RQ$9
'HVXOILQ\O)3DPLGH
'U\
:DWHU
5HFHLYLQJ
:RRG&DQ\RQ$9
)LSURQLO
'U\
:DWHU
5HFHLYLQJ
J/
:RRG&DQ\RQ$9
)LSURQLODPLGH
'U\
:DWHU
5HFHLYLQJ
J/
:RRG&DQ\RQ$9
)LSURQLOVXOILGH
'U\
:DWHU
5HFHLYLQJ
J/
:RRG&DQ\RQ$9
)LSURQLOVXOIRQH
'U\
:DWHU
5HFHLYLQJ
J/
:RRG&DQ\RQ$9
%LIHQWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
:RRG&DQ\RQ$9
'U\
:DWHU
5HFHLYLQJ
QJ/
:RRG&DQ\RQ$9
/DPEGDF\KDORWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
:RRG&DQ\RQ$9
3HUPHWKULQFLV
'U\
:DWHU
5HFHLYLQJ
QJ/
:RRG&DQ\RQ$9
3HUPHWKULQWUDQV
'U\
:DWHU
5HFHLYLQJ
QJ/
:RRG&DQ\RQ$9
'HVXOILQ\OILSURQLO
:HW
:DWHU
5HFHLYLQJ
J/
:RRG&DQ\RQ$9
'HVXOILQ\O)3DPLGH
:HW
:DWHU
5HFHLYLQJ
J/
:RRG&DQ\RQ$9
J/
:RRG&DQ\RQ$9
)LSURQLODPLGH
:HW
:DWHU
5HFHLYLQJ
J/
:RRG&DQ\RQ$9
)LSURQLOVXOILGH
)LSURQLO
:HW
:HW
:DWHU
:DWHU
5HFHLYLQJ
5HFHLYLQJ
J/
:RRG&DQ\RQ$9
)LSURQLOVXOIRQH
:HW
:DWHU
5HFHLYLQJ
J/
Citation - Abbrev.
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
(QVPLQJHUDQG.HOOH\D
Report/study Title
Region
2UDQJH&RXQW\
2UDQJH&RXQW\
2UDQJH&RXQW\
2UDQJH&RXQW\
2UDQJH&RXQW\
2UDQJH&RXQW\
Site(s)
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
:RRG&DQ\RQ$9
%LIHQWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
6DPSOHYDOXHPLVVLQJ
:RRG&DQ\RQ$9
:HW
:DWHU
5HFHLYLQJ
QJ/
6DPSOHYDOXHPLVVLQJ
:RRG&DQ\RQ$9
/DPEGDF\KDORWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
6DPSOHYDOXHPLVVLQJ
:RRG&DQ\RQ$9
3HUPHWKULQFLV
:HW
:DWHU
5HFHLYLQJ
QJ/
6DPSOHYDOXHPLVVLQJ
:RRG&DQ\RQ$9
3HUPHWKULQWUDQV
:HW
:DWHU
5HFHLYLQJ
QJ/
6DOW&UHHN6&
'HVXOILQ\OILSURQLO
'U\
:DWHU
'LVFKDUJH
J/
6DOW&UHHN6&
'HVXOILQ\O)3DPLGH
'U\
:DWHU
'LVFKDUJH
J/
6DOW&UHHN6&
)LSURQLO
'U\
:DWHU
'LVFKDUJH
6DOW&UHHN6&
)LSURQLODPLGH
'U\
:DWHU
'LVFKDUJH
6DOW&UHHN6&
)LSURQLOVXOILGH
'U\
:DWHU
'LVFKDUJH
J/
6DOW&UHHN6&
)LSURQLOVXOIRQH
'U\
:DWHU
'LVFKDUJH
J/
6DOW&UHHN6&
%LIHQWKULQ
'U\
:DWHU
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Timeframe
Pesticide (Analyte)
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Report/study Title
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Citation - Abbrev.
Report/study Title
Region
(QVPLQJHUHWDO
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Site(s)
3OHDVDQW*URYH&UHHN
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Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
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#
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%
Detected
Units
Sed. Unit
Weight
Mean
Median
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Citation - Abbrev.
Report/study Title
Region
Site(s)
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Timeframe
Pesticide (Analyte)
Wet/Dry
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Detected
Units
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Citation - Abbrev.
*DQHWDO
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Report/study Title
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Timeframe
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&HQWUDO&DOLIRUQLD
6RXWKHUQ&DOLIRUQLD
6RXWKHUQ&DOLIRUQLD
Units
Sed. Unit
Weight
6XLVXQ&UHHN
6XLVXQ&UHHN
6XLVXQ&UHHN
&\IOXWKULQ
&\SHUPHWKULQ
3HUPHWKULQ
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6HGLPHQW
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6DQ/RUHQ]R&UHHN
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6HGLPHQW
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5HFHLYLQJ
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JNJ
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6HGLPHQW
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QJ/
'U\
&\IOXWKULQ
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:DWHU
5HFHLYLQJ
QJ/
QJ/
Site(s)
&ROH&UHHN
/RQJ&DQ\RQ&KDQQHO
/RQJ&DQ\RQ&KDQQHO
/RQJ&DQ\RQ&KDQQHO
/RQJ&DQ\RQ&KDQQHO
/RQJ&DQ\RQ&KDQQHO
5LYHUVLGH&RXQW\
5HSRUW$SSHQGL[*
6RXWKHUQ&DOLIRUQLD
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%LIHQWKULQ
:HW
:DWHU
5HFHLYLQJ
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:DWHU
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:DWHU
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:DWHU
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:DWHU
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0XUULHWD&UHHN
5LYHUVLGH&RXQW\
5LYHUVLGH&RXQW\
5HSRUW$SSHQGL[*
5HSRUW$SSHQGL[*
5HGKDZN&KDQQHO
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3HUPHWKULQ
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5HFHLYLQJ
3HUPHWKULQFLV
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:HW
:DWHU
5HFHLYLQJ
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:DWHU
5HFHLYLQJ
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:DWHU
5HFHLYLQJ
7HPHFXOD&UHHN
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QJ/
QJ/
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QJ/
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7HPHFXOD&UHHN
6RXWKHUQ&DOLIRUQLD
QJ/
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3HUPHWKULQ
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:DWHU
5HFHLYLQJ
%LIHQWKULQ
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:DWHU
5HFHLYLQJ
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1'UHVXOWVVXEVWLWXWHGDVWKHGHWHFWLRQOLPLWJ/8QLWFRQYHUVLRQV
PDGHIRUFRQVLVWHQF\
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PDGHIRUFRQVLVWHQF\
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PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
2QO\PHDQDQGPD[SURYLGHGLQGDWDVHW
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:DWHU
5HFHLYLQJ
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PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
QJ/
PDGHIRUFRQVLVWHQF\
PDGHIRUFRQVLVWHQF\
2QO\PHDQSURYLGHGLQGDWDVHW
QJ/
:DUP6SULQJV&KDQQHO
QJ/
:DUP6SULQJV&KDQQHO
7HPHFXOD&UHHN
Notes
7HPHFXOD&UHHN
Max
QJ/
7HPHFXOD&UHHN
Min
QJ/
7HPHFXOD&UHHN
Median
QJ/
6RXWKHUQ&DOLIRUQLD
Mean
QJ/
5HSRUW$SSHQGL[*
5LYHUVLGH&RXQW\
QJ/
/DPEGDF\KDORWKULQ
5HSRUW$SSHQGL[*
QJ/
6RXWKHUQ&DOLIRUQLD
5LYHUVLGH&RXQW\
&\SHUPHWKULQ
0XUULHWD&UHHN
%
Detected
QJ/
Citation - Abbrev.
Report/study Title
Region
Site(s)
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
'LVFKDUJH0RQLWRULQJ5HSRUW
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
:DUP6SULQJV&KDQQHO
:DUP6SULQJV&KDQQHO
1DWRPDV67$
1DWRPDV67$
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
&\SHUPHWKULQ
/DPEGDF\KDORWKULQ
$OOHWKULQ
%LIHQWKULQ
:HW
:HW
:HW
:HW
:DWHU
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5HFHLYLQJ
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QJ/
QJ/
QJ/
Notes
PDGHIRUFRQVLVWHQF\
QJ/
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
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1DWRPDV67$
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Citation - Abbrev.
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
Report/study Title
Region
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
Site(s)
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
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1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
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1DWRPDV67$
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1DWRPDV67$
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1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
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1DWRPDV67$
1DWRPDV67$
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6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6XPS
6XPS
6XPS
6XPS
6XPS
6XPS
'HOWDPHWKULQ7UDORPHWKULQ
(VIHQYDOHUDWH
)HQSURSDWKULQ
)HQYDOHUDWH
)OXYDOLQDWH
/&\KDORWKULQ
3HUPHWKULQ
3UDOOHWKULQ
5HVPHWKULQ
7HWUDPHWKULQ
$OOHWKULQ
%LIHQWKULQ
&\IOXWKULQ
&\SHUPHWKULQ
'DQLWRO
'HOWDPHWKULQ
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
Citation - Abbrev.
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
Report/study Title
Region
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
Site(s)
6DFUDPHQWR&$
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
6XPS
6XPS
6XPS
6XPS
6XPS
6XPS
6XPS
6XPS
6XPS
6XPS
6XPS
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
(VIHQYDOHUDWH
)HQSURSDWKULQ
)HQYDOHUDWH
)OXYDOLQDWH
/&\KDORWKULQ
3HUPHWKULQ
3UDOOHWKULQ
5HVPHWKULQ
7HWUDPHWKULQ
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
$OOHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
%LIHQWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
&\IOXWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
&\SHUPHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
'HOWDPHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
'U\
6HGLPHQW
(VIHQYDOHUDWH
'U\
6HGLPHQW
'U\
)HQSURSDWKULQ
%
Detected
Units
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
JNJ
JNJ
5HFHLYLQJ
5HFHLYLQJ
6HGLPHQW
5HFHLYLQJ
'U\
6HGLPHQW
5HFHLYLQJ
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
'U\
'U\
JNJ
'U\
JNJ
'U\
JNJ
'U\
JNJ
'U\
JNJ
'U\
JNJ
'U\
JNJ
'U\
1'VXEVWLWXWHGDVKDOIWKH5/
)OXYDOLQDWH
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
/&\KDORWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
3HUPHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
7HWUDPHWKULQ
$OOHWKULQ
%LIHQWKULQ
'U\
'U\
'U\
6HGLPHQW
6HGLPHQW
6HGLPHQW
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
JNJ
JNJ
JNJ
'U\
'U\
'U\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
&\IOXWKULQ
&\SHUPHWKULQ
'HOWDPHWKULQ
'U\
'U\
'U\
'U\
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
JNJ
JNJ
JNJ
JNJ
'U\
'U\
'U\
'U\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
5RDG
5RDG (VIHQYDOHUDWH
)HQSURSDWKULQ
)OXYDOLQDWH
/&\KDORWKULQ
3HUPHWKULQ
7HWUDPHWKULQ
'U\
'U\
'U\
'U\
'U\
'U\
'U\
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
JNJ
JNJ
JNJ
JNJ
JNJ
JNJ
JNJ
'U\
'U\
'U\
'U\
'U\
'U\
'U\
$OOHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
%LIHQWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
5RDG
5RDG
5RDG
5RDG
&\IOXWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
&\SHUPHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
'HOWDPHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
(VIHQYDOHUDWH
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
)HQSURSDWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
)OXYDOLQDWH
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
/&\KDORWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
3HUPHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
7HWUDPHWKULQ
'U\
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
$OOHWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
%LIHQWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
&\IOXWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
&\SHUPHWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG 6DFUDPHQWR&RXQW\
Timeframe
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
Citation - Abbrev.
Report/study Title
Region
Site(s)
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&RXQW\
6DFUDPHQWR&$
6DFUDPHQWR&$
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
Median
Min
Max
Notes
)HQSURSDWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
)OXYDOLQDWH
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
/&\KDORWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
3HUPHWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
7HWUDPHWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
$OOHWKULQ
%LIHQWKULQ
&\IOXWKULQ
&\SHUPHWKULQ
:HW
:HW
:HW
:HW
:HW
:HW
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
JNJ
JNJ
JNJ
JNJ
JNJ
JNJ
'U\
'U\
'U\
'U\
'U\
'U\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
)HQSURSDWKULQ
)OXYDOLQDWH
/&\KDORWKULQ
3HUPHWKULQ
7HWUDPHWKULQ
:HW
:HW
:HW
:HW
:HW
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
6HGLPHQW
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
JNJ
JNJ
JNJ
JNJ
JNJ
'U\
'U\
'U\
'U\
'U\
$OOHWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
%LIHQWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
&\IOXWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
&\SHUPHWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
)HQSURSDWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
)OXYDOLQDWH
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
/&\KDORWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
3HUPHWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
7HWUDPHWKULQ
:HW
6HGLPHQW
5HFHLYLQJ
JNJ
'U\
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
Timeframe
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG 5RDG
5RDG
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$OOHWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
%LIHQWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
&\IOXWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
&\SHUPHWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
'DQLWRO
'U\
:DWHU
5HFHLYLQJ
QJ/
'HOWDPHWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
(VIHQYDOHUDWH
'U\
:DWHU
5HFHLYLQJ
QJ/
)HQYDOHUDWH
'U\
:DWHU
5HFHLYLQJ
QJ/
)OXYDOLQDWH
'U\
:DWHU
5HFHLYLQJ
QJ/
/&\KDORWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
3HUPHWKULQ
3UDOOHWKULQ
'U\
'U\
:DWHU
:DWHU
5HFHLYLQJ
5HFHLYLQJ
QJ/
QJ/
5HVPHWKULQ
'U\
:DWHU
5HFHLYLQJ
QJ/
$OOHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
%LIHQWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
&\IOXWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
&\SHUPHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
'DQLWRO
:HW
:DWHU
5HFHLYLQJ
QJ/
'HOWDPHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
(VIHQYDOHUDWH
:HW
:DWHU
5HFHLYLQJ
QJ/
)HQYDOHUDWH
:HW
:DWHU
5HFHLYLQJ
QJ/
Citation - Abbrev.
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
Report/study Title
Region
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
Site(s)
$UFDGH&UHHNDW:DWW
$YHQXH
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
)OXYDOLQDWH
/&\KDORWKULQ
:HW
:HW
:DWHU
:DWHU
5HFHLYLQJ
5HFHLYLQJ
3HUPHWKULQ
:HW
:DWHU
5HFHLYLQJ
3UDOOHWKULQ
:HW
:DWHU
5HFHLYLQJ
5HVPHWKULQ
$OOHWKULQ
%LIHQWKULQ
&\IOXWKULQ
&\SHUPHWKULQ
'DQLWRO
'HOWDPHWKULQ
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
/DJXQD&UHHNDW+Z\
(VIHQYDOHUDWH
:HW
:DWHU
5HFHLYLQJ
QJ/
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
5RDG
5RDG
5RDG
5RDG
5RDG
5RDG
)HQYDOHUDWH
)OXYDOLQDWH
/&\KDORWKULQ
3HUPHWKULQ
3UDOOHWKULQ
5HVPHWKULQ
:HW
:HW
:HW
:HW
:HW
:HW
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
5HFHLYLQJ
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
$OOHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
%LIHQWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
&\IOXWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
&\SHUPHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
'DQLWRO
:HW
:DWHU
5HFHLYLQJ
QJ/
'HOWDPHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
(VIHQYDOHUDWH
:HW
:DWHU
5HFHLYLQJ
QJ/
)HQYDOHUDWH
:HW
:DWHU
5HFHLYLQJ
QJ/
)OXYDOLQDWH
:HW
:DWHU
5HFHLYLQJ
QJ/
/&\KDORWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
3HUPHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
3UDOOHWKULQ
:HW
:DWHU
5HFHLYLQJ
QJ/
5HVPHWKULQ
$OOHWKULQ
%LIHQWKULQ
&\IOXWKULQ
&\SHUPHWKULQ
'DQLWRO
'HOWDPHWKULQ
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
5HFHLYLQJ
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
1DWRPDV67$
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
(VIHQYDOHUDWH
)HQYDOHUDWH
)OXYDOLQDWH
/&\KDORWKULQ
3HUPHWKULQ
3UDOOHWKULQ
5HVPHWKULQ
$OOHWKULQ
%LIHQWKULQ
&\IOXWKULQ
&\SHUPHWKULQ
'DQLWRO
'HOWDPHWKULQ
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:HW
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
:DWHU
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
'LVFKDUJH
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
QJ/
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
6WURQJ5DQFK6ORXJK
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Citation - Abbrev.
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
Report/study Title
Region
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
Site(s)
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
6XPS
6XPS
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Citation - Abbrev.
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
Report/study Title
Region
6DFUDPHQWR&$
6DFUDPHQWR&$
Site(s)
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
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Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
QJ/
Mean
Median
Min
Max
Notes
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Citation - Abbrev.
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&RXQW\
Report/study Title
Region
6DFUDPHQWR&$
6DFUDPHQWR&$
6DFUDPHQWR&$
Site(s)
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
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/DJXQD&UHHNDW+Z\
6DFUDPHQWR&RXQW\
6DFUDPHQWR&$
6DFUDPHQWR&$
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
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$UFDGH&UHHNDW:DWW
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Notes
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
$UFDGH&UHHNDW:DWW
$YHQXH
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6DFUDPHQWR&RXQW\
Timeframe
7DX)OXYDOLQDWH
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QJ/
$YHQXH
/DJXQD&UHHNDW+Z\
/DJXQD&UHHNDW+Z\
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Citation - Abbrev.
Report/study Title
Region
Site(s)
5RDG
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Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
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Timeframe
Citation - Abbrev.
9HQWXUD&RXQW\
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Report/study Title
Region
Site(s)
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
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#
#
%
Detected
Units
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Sed. Unit
Weight
J/
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Timeframe
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Mean
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Notes
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Max
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Median
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Citation - Abbrev.
9HQWXUD&RXQW\
Report/study Title
Region
Site(s)
9HQWXUD&RXQW\
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Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
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Timeframe
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Citation - Abbrev.
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Report/study Title
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Site(s)
Timeframe
Pesticide (Analyte)
Wet/Dry
Weather
Water/
Sediment
Discharge/
Receiving Water
#
#
%
Detected
Units
Sed. Unit
Weight
Mean
Median
Min
Max
Notes
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Report/study Title
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Max
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Report/study Title
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Site(s)
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#
#
%
Detected
Units
Sed. Unit
Weight
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Min
Max
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Review of Pyrethroid, Fipronil and Toxicity Monitoring Data

Transcription

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