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Small-Scale Trials Suggest Increasing Applications of Natular™ XRT and Natular™ T30 Larvicide Tablets May Not Improve Mosquito Reduction in Some Catch Basins

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Environmental Health Insights
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Stormwater catch basins are commonly treated with larvicides by mosquito control agencies to reduce local populations of mosquito species capable of transmitting West Nile virus. Recent evidence suggests that extended-release larvicides formulated to last up to 180 days in catch basins may not be effective in some basins due to chronic flushing, rapid dissolution, or burying of treatment in sump debris. To investigate if increasing the number of applications could improve effectiveness, a small study was performed over 13 weeks in 2015 to evaluate two extended-release larvicides (Natular™ XRT 180-day tablets and Natular™ T30 30-day tablets) and a larvicide oil (CocoBear™). Over the course of 13 weeks, three groups of eight basins were monitored for mosquitoes, each group receiving Natular™ XRT, Natular™ T30, or CocoBear™ larvicides. All basins received a single application at the beginning of the study period. Once mosquitoes in a basin surpassed the treatment threshold during weekly monitoring, an additional application of the associated larvicide was given to that basin. The number of applications during the study period ranged from 1 to 10 for CocoBear™ basins, 1 to 7 for T30 basins, and 2 to 8 for XRT basins. Overall, the average number of applications and the cost of larvicide per basin were 4.4 applications at $0.66 per Coco-Bear™ basin, 4.4 applications at $6.26 per T30 basin, and 4 applications at $16.56 per XRT basin. Basins treated with XRT and T30 needed reapplications more often than expected, yet were no more effective than CocoBear™, suggesting that increasing the frequency of application of these larvicide formulations may not provide increased mosquito reduction in some basins.
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ENVIRONMENTAL HEALTH INSIGHTS 2016:10
Introduction
Stormwater catch basins are common sources of permanent
or semipermanent standing water that are routinely tar-
geted for mosquito larvicide applications by local mosquito
control programs to reduce local mosquito populations and
incidence of mosquito-borne diseases.1–16 A common prac-
tice is to treat the stagnant water in all or most of the tens
of thousands or sometimes hundreds of thousands of basins
that can exist in an agency’s operational area with at least one
application of an extended-release larvicide formulated to last
up to 150–180 days. Since the mid-1990s, extended-release
larvicides (eg, Altosid® XR, FourStar®, and Natular™ XRT)
have been used by the North Shore Mosquito Abatement Dis-
trict (NSMAD), a publicly funded mosquito control agency
serving the northeast Chicago metropolitan area, to reduce
mosquitoes in 50,000 catch basins each season. Extended-
release larvicide formulations are appealing logistically as a
single treatment could theoretically reduce mosquito larvae
and pupae for an entire season (ie, May through September).
However, there is growing evidence that these products do not
provide control for as long as expected.17–2 3 e cause of the
control failures is not well understood but is likely related to
the catch basins’ structure, hydrology, and characteristics of
the sediments and debris that they collect. Recently, analy-
ses from three years of small-scale larvicide eectiveness tri-
als conducted by NSMAD20 and a year of district-wide catch
basin monitoring21 revealed that extended-release larvicide
applications fail to control mosquitoes in a signicant portion
of basins. Because catch basins capture and retain runo and
debris, extended-release larvicides applied to these structures
may be susceptible to being ushed out of basins, dissolving
more rapidly than designed, or becoming buried in debris cap-
tured in the sump. All of these phenomena can inuence the
eectiveness of larvicides.
e objective of this project was to determine if additional
applications of extended-release larvicides could improve the
eectiveness of these products in basins in which ushing, rapid
dissolution, or burying may occur. To do this, three mosquito
larvicides, Natular™ XRT 180-day tablet (Clarke Mosquito
Control Products, Inc.), Natular™ T30 30-day tablet (Clarke
Mosquito Control Products, Inc.), and CocoBear™ larvicide
oil (Clarke Mosquito Control Products, Inc.), were evaluated
Small-Scale Trials Suggest Increasing Applications of
Natular™ XRT and Natular™ T30 Larvicide Tablets May
Not Improve Mosquito Reduction in Some Catch Basins
Justin E. Harbison1, 2, Marlon Henry2, Peter C. Corcoran2, Dave Zazra2 and Christopher Xamplas2
1Department of Public Health Sciences, Loyola University Medical Center, Loyola Universit y Chicago, Maywood, IL, USA. 2North Shore
Mosquito Abatement District, Nor thfield, IL, USA.
A BS TR A CT: Stormwater catch basins are commonly treated with lar vicides by mosquito control agencies to reduce local populations of mosquito species
capable of transmitting West Nile virus. Recent evidence suggests that extended-release lar vicides formulated to last up to 180 days in catch basins may
not be eective in some basins due to chronic ushing, rapid dissolution, or bur ying of treatment in sump debris. To investigate if increasing the number
of applications could improve eectiveness, a smal l study was performed over 13 weeks in 2015 to evaluate two extended-release larvicides (Natular™
XRT 180-day tablets and Natular™ T30 30-day tablets) and a lar vicide oil (CocoBear™). Over the course of 13 weeks, three groups of eight basins were
monitored for mosquitoes, each group receiving Natular™ XRT, Natular™ T30, or CocoBear™ larv icides. All basins received a single application at the
beginning of the study period. Once mosquitoes in a basin surpassed the treatment threshold during week ly monitoring, an additional application of the
associated lar vicide was given to that basin. e number of applications during the study period ranged from 1 to 10 for CocoBear™ basins, 1 to 7 for T30
basins, and 2 to 8 for XRT basins. Overall, the average number of applications and the cost of larvicide per basin were 4.4 applications at $0.66 per Coco-
Bear™ basin, 4.4 applications at $6.26 per T30 basin, and 4 applications at $16.56 per XRT basin. Basins treated with XRT and T30 needed reapplications
more often than expected, yet were no more eective than CocoBear™, suggesting that increasing the frequency of application of these lar vicide formula-
tions may not prov ide increased mosquito reduction in some basins.
KEYWORDS: larv icide, catch basins, mosquitoes, cost
CI TATI ON: Harbi son et al. Sm all-S cale Trials S uggest In creasi ng Appli cation s of
Natular™ XRT and Natular™ T30 Larvicide Tablets May Not Improve Mosquito
Reduction in Some Catch Basins. Environmental Health Insights 2016:10 31–34
doi: 10.4137/EHI.S36722.
TYPE: Sho rt Repo rt
RECEIVED: October 20, 2 015. RESUBMITTED: November 18, 2 015. ACCEPTE D FOR
PUBLICATION: Novemb er 20, 2015.
ACADEMI C EDITOR: Timothy Ke lley, Editor in C hief
PEER RE VIEW: Fiv e peer revie wers con tribute d to the pee r review rep ort. Rev iewers’
repor ts total ed 1009 wor ds, exclud ing any con dentia l commen ts to the ac ademic ed itor.
FUNDING: Aut hors dis close no ex ternal funding s ources.
COMPET ING INTE RESTS: Au thors di sclose n o potentia l conic ts of inter est.
CORRESPONDENCE: jharbison@luc.edu
COPYRIGHT: © the autho rs, publi sher and li censee L ibert as Acade mica Limi ted. This i s
an open- access arti cle distr ibuted under the te rms of the Cr eative Co mmons CC -BY-NC
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Harbison et al
32
ENVIRONMENTAL HEALTH INSIGHTS 2016:10
during the 2015 season in catch basins located in the same
small residential area used for previous larvicide trials.20
Methods
All trials were conducted between June and September
2015 in catch basins located within a 0.7 km2 residential
area near the center of the NSMAD operational area. As
the study area has been used in previous NSMAD catch
basin studies, there were several years of data on the present
study’s catch basins to inform the present trials. Prior analy-
ses found that extended-release larvicides failed to exhibit
any control of mosquitoes over three consecutive years for
12 individual catch basins in the study area. erefore,
each of the three larvicides, XRT, T30, and CocoBear™,
was randomly assigned to eight basins that included four of
these failure basins and four in which larvicides appeared to
be eective. XRT is formulated with 6.25% spinosad, T30
is formulated with 8.33% spinosad, and CocoBear™ is for-
mulated with 10% mineral oil. CocoBea r™ is not considered
as an extended-release larvicide but was included for control
purposes to compare the extended-release larvicides (one
and three applications expected, respectively, for XRT and
T30) with a larvicide in which weekly reapplications would
be expected. e use of untreated basins as a more strin-
gent control was not incorporated in this study over concerns
of that these untreated basins could pose a risk to residents
within and near the study area.
Beginning the rst week of June and ending the rst
week of September, each of the 24 study basins was monitored
for the presence of mosquito larvae and pupae by removing the
circular grate of each structure with a manhole hook and taking
two dip samples using a standard 350-mL dipper. Mosquitoes
collected in a dip sample were counted, with the number of
pupae and fourth instar larvae noted. All 24 basins received
their respective larvicide treatments in the second week of
monitoring. Each subsequent week, a basin was found to have
reached or surpassed an average of 12 mosquito larvae and/or
pupae per dip, and that basin received an additional treatment
of its respective larvicide. e 12-mosquito threshold was
found by dip samples taken from untreated basins in the study
area from 2011 to 2014 that showed that the average number
of mosquitoes from a total of 1,752 dip samples in untreated
basins was 13.7 (95% condence interval [CI] = 12.5–14.9).
e total number (sum of two dips) of mosquitoes in basins
across weeks was compared among the treatments using a
repeated measures analysis of variance. e number and the
total cost of larvicide applications were also recorded each
week. In 2015 a single XRT tablet cost NSMAD $4.14,
$1.43 for a T30 tablet, and estimated $0.15 per single basin
for CocoBear™. Precipitation data were downloaded from a
nearby weather station of the National Oceanic and Atmo-
spheric Administration’s National Weather Service Forecast
Oce located at the Chicago O’Hare Airport (http://www.
nws.noaa.gov/climate/index.php?wfo=lot).
Results
All basins except two (one treated with CocoBear™ [CBa]
and one with T30 [T30h]) surpassed the threshold for retreat-
ment at least once (Table 1). e number of applications to
a single basin during the study period ranged from 1 to 10
for CocoBear™ basins, 1 to 7 for T30 basins, and 2 to 8
for XRT basins (Table 1). Generally, there did not appear
to be a large dierence among the eectiveness of larvicide
treatments each week (Table 2). e mean total mosquitoes
(sum of two dips) and 95% CI were 17.13 (11.58–22.67) for
CocoBear™ basins, 21.38 (15.05–27.70) for T30 basins, and
21.70 (14.97–28.43) for XRT basins over 12 weeks with active
treatment. ere was no statistical signicance found between
treatments: F (2, 21) = 0.32, P = 0.73. e percentages of the
fourth instars and pupae observed from the total mosquitoes
found among the treatments each week ranged from 6.9% to
87.9% for CocoBear™, 9.0% to 78.2% for T30, and 9.2% to
75.3% for XRT. e total number of applications to the eight
basins was 35 for CocoBear™ and T30 basins and 32 for XRT
basins. Overall, the average number of applications and the
cost of larvicide per basin were 4.4 applications at $0.66 per
CocoBear™ basin, 4.4 applications at $6.26 per T30 basin,
and 4 applications at $16.56 per XRT basin.
Discussion
Over the monitoring period, basins appeared to hold similar
numbers of mosquitoes across the three larvicide treatments,
suggesting, at least in the study basins, approximately equal
eectiveness for the amount and type of larvicides used. Cer-
tainly, it appears that the use of the extended-release tablets
(both XRT and T30) may not be the most cost-eective way
to reduce mosquitoes in the study basins. Most extended-
release basins needed more than the expected applications
throughout the monitoring period, yet their eectiveness was
no better than that of the oil. e use of the active ingre-
dient (spinosad) of two extended-release pesticides for mos-
quito control, including the eect on nontarget species, has
been described at length elsewhere.24 –30 Although larvicide
oils are not formulated to be eective for longer durations, it
did appear to be more cost eective than tablets in the study
basins. e cost of labor for larvicide applications appears to
be about the same for the three products as the total appli-
cations were similar. However, the cost of product is signi-
cantly lower for CocoBear™ per application, making it the
most economical treatment.
Larvicide oils are designed to leave a thin lm on the
surface of treated water potentially killing larvae and pupae
via contact or suocation. However, because thislm tends
to break down quickly when the water surface is disturbed
(eg, from an inux of rain and runo ), this type of larvi-
cide is considered to be eective for a much shorter dura-
tion than the extended-release larvicides. Alternatively, the
XRT and T30 tablets are formulated to slowly release their
active ingredients over time, killing mosquito larvae and
Increasing applications of Natular™ XRT and Natular™ T30 lar vicide tablets
33
ENVIRONMENTAL HEALTH INSIGHTS 2016:10
pupae through contact or ingestion. Since the NSMAD was
established in 1927 and until the mid-1990s, the larvicide
oils were predominantly applied to the district’s catch basins.
Oils are somewhat easier to apply than the extended-release
larvicides because often the applicator does not need to leave
his or her vehicle to treat basins using a long nozzle to spray
the larvicide into basins. As such, all NSMAD basins could
usually receive three to four oil treatments in a season. How-
ever, our results suggest that three to four applications of oil,
as well as T30 and XRT, may not be enough for some basins.
Currently, it takes approximately two months or more for
NSMAD technicians to treat all basins with extended-release
larvicides, and often most basins do not receive an additional
treatment before the seasonal technicians become unavail-
able. Looking for longer lasting alternatives to extended-
release tablets and more clearly identifying areas with a
signicant number of basins in which larvicides fail will be
important next steps.
Acknowledgment
e authors thank Roger S. Nasci for review and insightful
comments on the initial draft of this article.
Table 1. A comparison of the number of larvicide applications made to eight CocoBear™ oil-treated, eight Natular™ T30-treated, and eight
Natular™ XRT-treated catch basins from June to September 2015. T indicates that the threshold for treatment ($12 mosquitoes per dip) was
surpassed and an application of the associated larvicide to the basin was made.
WEEK NUM BER
BASIN 23 24 25 26 27 28 29 30 31 32 33 34 35 TO TAL
CocoBear Oil
CBa T 1
CBb T T T T T T 6
CBc T T 2
CBd T T T 3
CBe T T T T T T T T T T 10
CBf T T 2
CBg T T T T T 5
CBh T T T T T T 6
T30 30-day Tablets*
T30a T T T T T T T 7
T30b T T T 3
T30c T T T 3
T30d T T T T T 5
T30e T T T T 4
T30f T T T T T T 6
T30g T T T T T T 6
T30h T 1
XRT 180- day Tablets
XR Ta T T 2
XRTb T T T 3
XR Tc T T T T T 5
XR Td T T T T 4
XR Te T T T T T 5
XRTf T T T T T T T T 8
XR Tg T T 2
XRTh T T T 3
Note: aThe duration of T3 0 tablets is formulated to last fou r weeks, and three treatments would be expected for 13 weeks on weeks 23, 28, and 33.
Harbison et al
34 ENVIRONMENTAL HEALTH INSIGHTS 2016:10
Author Contributions
Conceived, designed, and performed the experiments: JEH,
MH. Analyzed the data: JEH, MH. Wrote the rst draft of
the article: JEH, DZ, CX, PCC, MH. All authors reviewed
and approved the nal article.
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24 0.0 ± 0.0 0.06 ± 0.06 0.0 ± 0.0 8.33
25 4.88 ± 1.95 5.56 ± 1.81 4.5 ± 1.99 3.1 8
26 7.25 ± 4.17 20.31 ± 5.5 4 12.06 ± 3.93 2.01
27 3.06 ± 1.64 7.87 ± 2.63 9.94 ± 3.78 2.1 8
28 5.37 ± 2.27 7.31 ± 1.46 11.19 ± 3.18 5.05
29 6.13 ± 2.25 1.12 ± 0.45 11.5 ± 3.45 0.00
30 17. 88 ± 4.9 6 18.88 ± 4.59 12.69 ± 3.03 1.35
31 4.44 ± 1.61 2.69 ± 0.96 1.19 ± 0.67 0.00
32 11.44 ± 3.93 18.63 ± 3.89 21.0 6 ± 7.47 0.94
33 3.63 ± 2.03 1.13 ± 0.64 1.31 ± 0.52 1.32
34 24.5 ± 6.07 27.81 ± 6.98 31.0 ± 5.1 1.88
35 14 .19 ± 3.67 16.88 ± 4.6 13.75 ± 5.88 0.00
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... Additionally, many long-lasting mosquito-killing formulations use materials such as calcium sulfate as a structural framework. 41,42 These materials are nontoxic, chemically stable and exhibit good physical properties. However, in heavy rain or high humidity conditions, such materials may absorb moisture, leading to an unstable framework, premature disintegration of the tablets, and failure of the sustained-release system. ...
Article
BACKGROUNDS To provide a long‐lasting formulation for spinosad (SP) targeting larval stages of Aedes aegypti (Linnaeus) and others alike, a SP tablet was developed based on microspheres, using polylactic acid as inside coating material. The microspheres were encapsulated using polyethylene glycol and 1‐hexadecanol to form a sustained‐release SP tablet. Micromorphology, active ingredient loading, structure identification, photolysis resistance, and biological activity were evaluated in this report. RESULTS (1) SP microspheres have an average particle size of 6.16 ± 2.28 μm, low adhesion, and good dispersion as evaluated by scanning electron microscopy (SEM) and morphology; (2) The average active ingredient loading and encapsulation of SP microspheres were 32.80 ± 0.74% and 78.41 ± 2.22%, respectively; (3) The chemical structure of encapsulated SP was confirmed by FT‐IR and ¹ H‐NMR; (4) The photostability of the microspheres and the tablets were evaluated. The results showed that DT 50 (time required to dissipate 50% of the mass originally present) of SP was 0.95 days in microspheres and 6.94 days in tablets. (5) The long‐term insecticidal activity of SP tablets was investigated, and the tablet had a long‐lasting activity against the mosquito larvae, showing 100% larval mortality for 63 days. CONCLUSIONS The study provided a new long‐lasting formulation of SP which displayed good efficacy in the control of Ae. aegypti larvae. This article is protected by copyright. All rights reserved.
... Mosquitoes are more likely to be found in catch basins with relatively low pH and high total suspended solids, carbon, and nitrogen (Butler et al. 2007, Gardner et al. 2013. Catch basins are designed to retain water and they also collect and retain debris, which may have an effect on performance of larvicides (Harbison et al. 2016). In this study we show that water hardness may be affected by the presence of the larvicide product itself. ...
Article
In response to apparent lack of efficacy of spinosad treatments of storm drain catch basins in Marathon, Florida, we investigated water quality parameters where drains had been treated with Natular® XRT extended release tablets. An analysis of water samples from these sites revealed that alkalinity and water hardness differed significantly between treated and untreated drains. However, when tested in a semi-field environment protected from runoff, differences in alkalinity were not associated with spinosad treatment, whereas water hardness increased over time in replicates treated with Natular XRT. Water quality may be a reason for poor larval control rather than product failure or resistance. Future work will investigate whether changes in water hardness associated with spinosad treatment may impact the efficacy of this larvicide at reducing adult emergence in field environments.
... Mosquitoes are more likely to be found in catch basins with relatively low pH and high total suspended solids, carbon, and nitrogen (Butler et al. 2007, Gardner et al. 2013. Catch basins are designed to retain water and they also collect and retain debris, which may have an effect on performance of larvicides (Harbison et al. 2016). In this study we show that water hardness may be affected by the presence of the larvicide product itself. ...
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The JFMCA (Journal of the Florida Mosquito Control Association) Vol 67, 2020 published 7 research articles, 7 scientific and operation notes, and submitted abstracts of the 91st annual meeting of the FMCA. The Journal has been published once a year.
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In the northeastern part of the greater Chicago metropolitan area, the North Shore Mosquito Abatement District (NSMAD) treats approximately 50,000 catch basins each season with larvicide tablets as part of its effort to reduce local populations of the West Nile virus (WNV) vector Culex pipiens. During the 2014 season, an NSMAD technician monitored a subset of 60-195 basins weekly for 18 weeks among the communities of the District for the presence of mosquitoes. Monitoring found no clear evidence in the reduction of mosquitoes with the use of larvicides, and visual inspections of 211 larvicide-treated basins found that the majority (162, 76.8%) were missing tablets 1-17 weeks after applications. This loss of treatment may be due to the rapid dissolution or flushing of larvicides and would help explain why the larvicide appeared to be ineffective.
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West Nile virus (WNV) became established in New York in 1999, in the first outbreak in the Western Hemisphere. WNV is propagated in many species of birds and has been detected in more than 300 bird spe-cies in the United States, although there are great differences in the viremia level among the various bird species. Culex mosquitoes, including Cx. restuans, the Cx. pipiens complex and Cx. tarsalis are important vectors of WNV in the USA. Laboratory transmission of WNV by Cx. pipiens form molestus showed that they were highly competent vectors of WNV, with infection and dissemination rates of 96% and 81%, respectively. Three species, including two of the Culex pipiens group (Cx. pipiens pallens (as pallens in this article) and Cx. pipiens form molestus (as molestus in this article)) and Aedes albopictus, account for more than 99% of collected mosquitoes surrounding Tokyo. The Cx. pipiens complex (pallens, molestus and Cx. quinquefasciatus) prefer both human and avian hosts, and there is no clear differences in avian blood-feeding patterns between pallens and molestus, but there are significant differences among mammal-ian species, with molestus preferring human blood compared with pallens. Ducks (mallards & spotbill ducks) and tree sparrows are major blood sources for the Cx. pipiens group in Japan, which are moderate or high amplifiers of WNV. From a larval bioassay with several kinds of insecticides it was demonstrated that etofenprox, a synthetic pyrethroid, exhibited relatively low effectiveness against several mosquito colonies of the Cx. pipiens group in an urban environment of Japan. The most important larval habitats of the Cx. pipiens group and Ae. albopictus are catch basins along public roads and this kind of structure should be targeted to control mosquito larvae.
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The tens of thousands of catch basins found in many urban areas are a primary target of local vector control agencies for seasonal application of extended-release larvicides. A concern with using larvicides in these structures is that active ingredients can be hampered by high flows, debris, and sediment, all of which are common to these structures. As such a certain proportion of basins may be "resistant" to larvicide treatments due to site specific characteristics that may promote these and other factors that hinder larvicide action and/or promote mosquito infestation. Analyses from three years of larvicide efficacy trials suggest that over a quarter of basins in the study area may not be receiving adequate protection from a single dose of larvicide that is routinely applied. Implications of increasing the dose and/or toxicity of larvicide treatments are discussed further.
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The primary mosquito species associated with underground stormwater systems in the United States are the Culex pipiens complex species. This group represents important vectors of West Nile virus (WNV) throughout regions of the continental U.S. In this study, we designed a mathematical model and compared it with surveillance data for the Cx. pipiens complex collected in Beaufort County, South Carolina. Based on the best fit of the model to the data, we estimated parameters associated with the effectiveness of public health insecticide (adulticide) treatments (primarily pyrethrin products) as well as the birth, maturation, and death rates of immature and adult Cx. pipiens complex mosquitoes. We used these estimates for modeling the spread of WNV to obtain more reliable disease outbreak predictions and performed numerical simulations to test various mosquito abatement strategies. We demonstrated that insecticide treatments produced significant reductions in the Cx. pipiens complex populations. However, abatement efforts were effective for approximately one day and the vector mosquitoes rebounded until the next treatment. These results suggest that frequent insecticide applications are necessary to control these mosquitoes. We derived the basic reproductive number (ℜ0) to predict the conditions under which disease outbreaks are likely to occur and to evaluate mosquito abatement strategies. We concluded that enhancing the mosquito death rate results in lower values of ℜ0, and if ℜ0<1, then an epidemic will not occur. Our modeling results provide insights about control strategies of the vector populations and, consequently, a potential decrease in the risk of a WNV outbreak.
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Stormwater catch basins are the primary source of mosquitoes targeted by the North Shore Mosquito Abatement District, in the northern suburbs of Chicago. Over a 17-wk period (June to September 2011), 3 clusters of catch basins located within a 0.7-km2 area were monitored weekly with dipper samples of immature mosquitoes. During the 2nd week of monitoring, Natular XRT tablets (6.25% spinosad) were applied to northernmost cluster and FourStar Briquets (6% Bacillus û, 1% Bacillus thuringiensis israelensis) were applied to the southernmost cluster; the remaining middle cluster was kept untreated. Following 15 wk of monitoring in 20 basins in each cluster, both Natular and FourStar reduced immature numbers in treated catch basins for 8 consecutive weeks. These results suggest, if effectively timed, a single application of either larvicide may last an entire season.
Article
Because it is often logistically impossible to monitor all catch basins within an operational area, local mosquito control programs will preemptively treat catch basins with larvicides each season. However, these larvicides can, ostensibly, be considered water quality pollutants. To experimentally reduce the use of larvicides toward improving water quality, 30 basins within a small 0.7-km(2) residential area were monitored weekly for the presence of larvae and pupae for 14 wk in the summer of 2013. Once a basin was found to reach a threshold of 12 mosquitoes per dip sample, it received a FourStar® Briquet (a 180-day briquet formulation of 6% Bacillus sphaericus and 1% B. thuringiensis israelensis). Each week a FourStar-treated basin surpassed this threshold, it was treated with an application of CocoBear™ oil (10% mineral oil). By the end of trials, all but one basin received a briquet and 13 required at least 4 treatments of CocoBear, suggesting that preemptive treatment is appropriate for the study area.
Article
The North Shore Mosquito Abatement District applies extended release larvicides including methoprene-based Altosid® XR Extended Residual Briquets to approximately 40,000 catch basins in the southern half of the District's operational area at the beginning of each season. Treatments begin in May and typically again 9 to 10 wk later when larvicide efficacy appears to wane. In 2013 spinosad-based Natular™ XRT tablets were applied to basins, and a subset were monitored for larvae and pupae weekly with a standard dipper. When setting the threshold for retreatment as 12 juveniles per dip sample it was observed that basins required a second application 9 wk after the initial application, a time period similar to Altosid despite utilizing a different active ingredient. Average counts of weekly larval samples appeared to be positively associated with average numbers of Culex pipiens collected the following week in a gravid trap located among catch basins, highlighting the importance of basins as sources of these mosquitoes.
Article
A Culex quinquefasciatus Say colony was selected for 45 generations at LC70-90 levels using Natular XRG, a granular formulation of 2.5% spinosad for induction of spinosad resistance. Resistance to spinosad was noticed in early generations (F1-F9). Resistance levels increased gradually from generations F11-F35, and elevated significantly from generation F37 through F47, when resistance ratios reached 2,845-2,907-fold at LC50 and 11,948-22,928-fold at LC90 The spinosad-resistant Cx. quinquefasciatus colony was found not to be cross-resistant to Bacillus thuringiensis israelensis (Bti), a combination of Bti and Bacillus sphaericus, methoprene, pyriproxyfen, diflubenzuron, novaluron, temephos, or imidacloprid. However, it showed various levels of cross-resistance to B. sphaericus, spinetoram, abamectin, and fipronil. Conversely, a laboratory colony of Cx. quinquefasciatus that is highly resistant to B. sphaericus did not show cross-resistance to spinosad and spinetoram. Field-collected and laboratory-selected Cx. quinquefasciatus that showed low to moderate resistance to methoprene did not show cross-resistance to spinosad and spinetoram. Mechanisms of cross-resistance among several biorational pesticides were discussed according to their modes of actions.
Article
A southern house mosquito Culex quinquefasciatus Say colony was established from surviving late instars and pupae from a semifield evaluation on Natular XRG (a granular formulation containing 2.5% spinosad). The initial lethal levels ofNatular XRG against this colony were determined in the laboratory for the first-generation progeny (designated as F1). Selection pressure was applied at LC70-90 levels to 10,000-15,000 late third- and early fourth-instar larvae of each generation with Natular XRG. Susceptibility changes in response to selection were determined every other generation, where a gradual and steady decline in susceptibility occurred from generation F1 to F35, followed by significant decline from generations F37 to F45 For reference purposes, susceptibility of freshly collected wild populations as well as a laboratory colony of the same species was also determined concurrently, which fluctuated within a slightly wider range for the wild populations and a tighter range for the laboratory colony. By comparing with wild populations and laboratory reference colony, tolerance to spinosad was observed from generations up to F9 in the selected population. Resistance levels increased gradually from generation F11 to F35, and elevated significantly from generations F37 to F45, when resistance ratios reached 1,415.3- to 2,229.9-fold at LC50 and 9,613.1- to 17,062.6-fold at LC90. Possible mechanisms of resistance development to spinosad were discussed.
Article
We present data showing that structures serving as drains and catch basins for stormwater are important sources for production of the mosquito arbovirus vectors Aedes aegypti and Culex quinquefasciatus in Mérida City, México. We examined 1,761 stormwater drains - located in 45 different neighborhoods spread across the city - over dry and wet seasons from March 2012-March 2013. Of the examined stormwater drains, 262 (14.9%) held water at the time they were examined and123 yielded mosquito immatures. In total, we collected 64,560 immatures representing nine species. The most commonly encountered species were Cx. quinquefasciatus (n=39,269) and Ae. aegypti (n=23,313). Ae. aegypti and Cx. quinquefasciatus were collected during all 11 months when we found water-filled stormwater drains, and both were found in stormwater drains located throughout Mérida City. We also present data for associations between structural characteristics of stormwater drains or water-related characteristics and the abundance of mosquito immatures. In conclusion, stormwater drains produce massive numbers of Ae. aegypti and Cx. quinquefasciatus across Mérida City, both in the wet and dry seasons, and represent non-residential development sites that should be strongly considered for inclusion in the local mosquito surveillance and control program.