What is chlorantraniliprole?
Chlorantraniliprole is a human-made insecticide. It
is
in a class of
pesticides called anthranilic diamides.1 It
controls
moth and butterfly
caterpillars (larvae). It also controls some beetles and "true" bugs like aphids
and spittlebugs.2,3 Chlorantraniliprole was
first
registered for use in
2008.2
Technical Grade Chlorantraniliprole: This fact
sheet refers to the technical grade, or "pure"
chlorantraniliprole only. Products you buy from the store include other ingredients as well. While
many
of
the chemicals used as other ingredients may not pose health or environmental risks, some of them can
be
toxic. In some cases, the other ingredients can pose greater risks than the active ingredient
itself.
What are some products that contain chlorantraniliprole?
There are over 60 products that contain
chlorantraniliprole. Some of these
can only be used by licensed professionals. Products with chlorantraniliprole may be labeled for use on a
variety of fruits, vegetables, potatoes, and rice. They are also used on cotton, turf grass, ornamental
plants,
public landscaped areas, and as seed treatments. Products containing chlorantraniliprole may be granules,
concentrates, or liquids.2,4
Chlorantraniliprole
is
considered a reduced-risk
pesticide for certain uses by the U.S. Environmental Protection Agency (U.S. EPA).4 See the
text box about technical
grade
chlorantraniliprole.
How does chlorantraniliprole work?
Chlorantraniliprole binds to a specific receptor in muscles called the ryanodine receptor. When
chlorantraniliprole binds to this receptor, it causes muscle cells to leak calcium. The muscles stop
working
normally. The insect is paralyzed and dies. The ryanodine receptor is different in insects than in
mammals.
Chlorantraniliprole binds much more tightly to the receptor in insects.5,6 It is
toxic to insects mainly if it is eaten.7
Chlorantraniliprole is also toxic to
insect eggs, larvae, and pupae on contact.8,9
Chlorantraniliprole is based on the extract of Ryania speciosa, a plant that
grows in South America and the Caribbean.6
Scientists
realized in the 1940s that
Ryania speciosa is toxic to insects.10
Ryania extract was used as a
registered insecticide until 1996.2
Ryania
extract itself is no longer
used because it is very toxic to mammals.5,6
How might I be exposed to chlorantraniliprole?
You could be exposed to chlorantraniliprole while
using a product or being too close to an application.
You could get chlorantraniliprole on your skin, in your
eyes, or breathe it in. Granules may be mistaken for food
crumbs by very young children or pets. Very low levels
of chlorantraniliprole may be found in food and drinking
water.11,12
Pesticides used on food crops
have
tolerances.
See the text box about pesticide tolerances.
IMPORTANT: Always follow
label
instructions and take steps to minimize
exposure. If any exposures occur, be sure to follow the First
Aid instructions on the product label carefully. For additional treatment advice, contact
the Poison
Control
Center at 800-222-1222. If you wish to discuss
a
pesticide
problem, please call
NPIC at 800-858-7378.
Any chemical, including any
pesticide, can pose risks to people, pets, or the
environment. Understanding pesticide
risk will
help you take steps
to
minimize it.
The risk of a pesticide depends on two things,
exposure (how much?) and toxicity (how
poisonous?). The exposure is the amount you
get in or on your body, or the amount that is
released into the environment. The toxicity of
a pesticide is a measure of how poisonous it is
to people or the environment. Even products
that are low in toxicity can be hazardous if the
exposure is high enough. Take steps to lower
your chance of exposure to reduce your risk.
Chlorantraniliprole is very low in toxicity to people and other
mammals. Chlorantraniliprole does not irritate skin. It may be slightly irritating to the
eyes.
It
is not a
skin
sensitizer.4 See
the
text
box about
pesticide
risk.
If chlorantraniliprole is eaten, it is very low in toxicity.4 A person
who drank a product containing chlorantraniliprole had abnormal heart function.13
Chlorantraniliprole caused some minor eye irritation in rabbits, but all signs of irritation
disappeared in
72
hours.4 No other
symptoms
from
exposure were
found at
the time this fact sheet
was written. For more information about how NPIC finds scientific studies, see our page on
Writing NPIC Fact Sheets.
Rats fed very high doses of chlorantraniliprole had small changes to the
adrenal
glands. Scientists did not
consider this harmful although it was treatment related.4
TOXICITY
CLASSIFICATION -
CHLORANTRANILIPROLE4 (see the text
box about mg/kg)
| High Toxicity |
Moderate Toxicity |
Low Toxicity |
Very Low Toxicity |
Acute Oral LD50 |
≤ 50 mg/kg |
> 50-500 mg/kg |
> 500-5000 mg/kg |
>5000 mg/kg |
Inhalation LC50 |
≤ 0.05 mg/L |
> 0.05-0.5 mg/L |
> 0.5-2.0 mg/L |
> 2.0 mg/L |
Dermal LD50 |
≤ 200 mg/kg |
> 200-2000 mg/kg |
> 2000-5000 mg/kg |
> 5000 mg/kg |
Primary Eye Irritation |
Corrosive (irreversible destruction of ocular tissue) or corneal
involvement or
irritation
persisting for more than 21 days |
Corneal involvement or other eye irritation clearing in 8 - 21 days |
Corneal involvement or other eye irritation clearing in 7 days or less |
Minimal effects clearing in less than 24 hours |
Primary Skin Irritation |
Corrosive (tissue destruction into the dermis and/or scarring) |
Severe irritation at 72 hours (severe erythema or edema) |
Moderate irritation at 72 hours (moderate erythema) |
Mild or slight irritation at 72 hours (no irritation or
erythema) |
The shaded boxes reflect signs and symptoms observed after a brief exposure.
Modeled after
the
U.S.
Environmental Protection Agency, Office of Pesticide Programs, Label Review
Manual, Chapter
7:
Precautionary Statements.
https://www.epa.gov/sites/default/files/2018-04/documents/chap-07-mar-2018.pdf.
Data
from EPA 1998,
Reregistration Eligibility Decision (RED) for Bacillus
thuringiensis.
You may be wondering why the "High Toxicity" column has smaller
numbers than
the
"Low Toxicity"
column. This is because if a smaller amount of the pesticide caused a health
effect, it's
more
toxic. If it takes a larger amount of the pesticide to cause a health effect,
it's less
toxic.
|
What happens to chlorantraniliprole when it
enters the body?
Healthy skin blocks most chlorantraniliprole from entering the body. Less than 3% of a dose
of
chlorantraniliprole passed through skin in a study with rats. Chlorantraniliprole was found
in many places
in
the body after a single dose was eaten by animals. It is not expected to build up in the
body.11
Rats given chlorantraniliprole absorbed most of it in 5-12 hours. They excreted nearly all of
it in 48-72
hours,
mostly in feces but also in urine. The half-life in blood plasma was 38-82 hours.
Chlorantraniliprole is
broken
down in the body into a number of other chemicals. The type of chemicals may depend on the
species of
animal.11 The
U.S. EPA considers these
breakdown
chemicals to be less toxic than
chlorantraniliprole.4
Scientists fed a goat 10 mg/kg chlorantraniliprole for a week. They also fed hens the same
dose for two
weeks.
Less than 1% of the dose was recovered in the goat's milk, and less than 4% was recovered in
eggs.4,14
"Mg/kg" is a way to measure a chemical dose. This can tell us how toxic a chemical
is. "Mg" means
milligrams
of a chemical. "Kg" means one kilogram of an animal's body weight. Something that is
highly toxic
may
kill a
person with a very small amount of chemical. If something is very low in toxicity,
it may take much
more
for
that same person to
become very sick or die.
Is chlorantraniliprole likely to contribute to
the
development
of cancer or birth defects?
Chlorantraniliprole is classified as "not likely to be carcinogenic to humans" by the U.S.
EPA.11 Test
animals did not develop more
tumors
than
expected when they were exposed
to chlorantraniliprole. Chlorantraniliprole does not cause gene mutations that damage DNA.
It is not
considered
toxic to the immune system.4,7
Chlorantraniliprole does not seem to cause birth defects. Scientists fed mother rats and
rabbits up to 1,000
mg/kg per day during their pregnancies. They did not see any effects on the babies.4,11 When
scientists fed rats
chlorantraniliprole for
two generations, the rats'
reproduction was not affected.4
Has anyone studied non-cancer effects from
long-term exposure
to
chlorantraniliprole?
Scientists gave rats, mice, and dogs chlorantraniliprole in their food for up to two
years. They saw no
evidence
of harm at high doses within the range of 1,000-1,500 mg/kg/day. Scientists saw some
changes in the rats'
adrenal glands' cell structure but no change in how the glands worked. The rats, mice,
and dogs had some
small
increases in liver weight.4
No information was found regarding endocrine disruption by chlorantraniliprole at the
time this fact sheet
was
written. For more information about how NPIC finds scientific studies, see our page on
Writing NPIC Fact
Sheets.
Other scientists force fed rats a commercial pesticide product with chlorantraniliprole
and other ingredients
every day for 28 days. The rats received a very high dose of 3,750 mg/kg of
chlorantraniliprole. Rats in
this
group gained less weight than rats in the other groups. When the scientists force fed
rats the same
pesticide
product every other day for 90 days at the lower doses of 375 or 187.5 mg/kg, the rats
gained less weight
than
rats which got less or none of the pesticide product. Rats who received smaller amounts
gained the same
weight
as control rats in both groups.15
Are children
more sensitive to
chlorantraniliprole than
adults?
Children are not expected to be more sensitive to chlorantraniliprole than adults.4 However,
children may act in ways that put
them at
greater risk of being
exposed. For example, they may spend more time on the ground. They
may also be more likely to place their hands in their mouths after touching treated areas.
Chlorantraniliprole is persistent and mobile in the environment.
It does
not easily dissolve in water but moves in the environment because it does
not bind well to soil. It breaks down in soil very slowly, with half-lives of up to
1,130
days.4
Soil temperature,
aging, and
pH affect how
long
chlorantraniliprole lasts.
Sunlight can also break down residues on soil. In water, chlorantraniliprole is
broken down by
reactions
with
light. It also reacts with water, particularly in alkaline water.16
Its half-lives ranged from 10-22 days17
to
228-924 days
in aerobic soils. The
half-life on bare ground ranged from 52 to 1,130 days.7 When
chlorantraniliprole
was sprayed on rice fields at twice the labeled rate, the half-life of the pesticide
in the soil was
16
days,
and less than one day in water. The half-life of the pesticide in rice straw was 3.5
days.18
When
chlorantraniliprole was
applied to
maize
straw, its half-lives were 9 to
11 days.17 It
is expected
to build
up in
soil
where it
is used
continuously.4 See
our
fact sheet to
learn
more
about
pesticide
half-life.
Chlorantraniliprole breaks down in the environment to form other chemicals. At least
five breakdown
chemicals
have been found in soil. Three others have been found in water in laboratory tests.
However,
scientists do
not
expect either the formulated products or the breakdown chemicals to be more toxic
than pure
chlorantraniliprole.4
In water, both sunlight and chemical reactions down chlorantraniliprole.4 The
reactions and the breakdown chemicals depend on water acidity.19
Scientists made biochar
from walnut shells. The
biochar did not affect the
half-life or breakdown rate of chlorantraniliprole.20
However, biochar affects
the binding of chlorantraniliprole depending on the soil or biochar type. Different
types of biochar
decreased
how much chlorantraniliprole earthworms absorbed.21
Can chlorantraniliprole affect birds, fish,
or other
wildlife?
Chlorantraniliprole is practically non-toxic to birds when the birds are exposed for short
periods of
time.
Bobwhite quail and mallards were fed high doses of chlorantraniliprole for longer periods of
time. When
bobwhite
quail ate 20.7 mg/kg of chlorantraniliprole per day, the shells of their eggs were 9%
thinner. When
mallard
ducks ate 133 mg/kg of chlorantraniliprole per day, their eggs had fewer live embryos after
3 weeks of
incubation. According to the U.S. EPA, there is "no evidence of chlorantraniliprole
toxicity" to
mammals.16
Some researchers found that products with chlorantraniliprole should not harm beneficial
predatory
insects or
bees when used according to the label.8,22,23,24
Chlorantraniliprole is low in
toxicity to parasitic wasps.8
Other scientists have studied the effects of chlorantraniliprole on bees. They found that
when honeybee
larvae
were fed doses of products containing chlorantraniliprole at low doses of 0.087-0.139
μg/chlorantraniliprole
per
larva per day, many of them died before becoming adult bees.16
Another group of
scientists exposed bumblebees to chlorantraniliprole in a pollen and honey mixture. The
mixture
contained
0.615
mg/kg of chlorantraniliprole. The bumblebees ate the mixture for 30 days. They ate the same
amount of
pollen
as
control colonies that were not fed chlorantraniliprole. Colonies with queens showed no
effects on
reproduction
or behavior.25 However, the U.S. EPA has
concluded
that bumblebees may be more
sensitive than honeybees to pesticide products with chlorantraniliprole.16
As expected, chlorantraniliprole is toxic to butterflies and moths.3 Monarch
butterfly eggs were killed by chlorantraniliprole at very low doses of 0.018 μg/g per egg.
Chlorantraniliprole
was also toxic to the monarch caterpillars when they ate leaves with residues of even lower
doses. When
researchers treated pupae with 0.04 μg/g of chlorantraniliprole, the butterflies did not
emerge.9
Chlorantraniliprole is not very toxic to most soil invertebrates including
earthworms.7
Scientists exposed
earthworms
to
chlorantraniliprole at several low
concentrations in the soil for 42 days. The concentrations of chlorantraniliprole were 0.1,
1.0, 5.0,
and
10.0
mg/kg in soil. The residue built up in the earthworms' bodies. The earthworms lost weight
and had fewer
young
at the two highest doses.26
Chlorantraniliprole
at
high doses of 1,000 mg/kg did
not affect soil isopods. One species of oribatid soil mite and a small white worm called an
enchytraeid
also
showed no effects. The amount of
organic matter in soil helped reduce the effects of chlorantraniliprole on
springtails. However, very low amounts of 0.14 mg of chlorantraniliprole per
kg of dried soil affected their reproduction. Scientists expect these levels to
happen in the field under current use.27
Short, one-time exposures to chlorantraniliprole are low in toxicity to fish. However, fish
were more
sensitive
when exposed over longer periods of time.4,16
According to the U.S. EPA, risks of
direct effects to amphibians are "below Agency screening levels of concern."4 No
direct or indirect impacts to amphibians or reptiles are expected.7
Chlorantraniliprole is considered highly toxic to aquatic invertebrates.4
Chlorantraniliprole was highly toxic to crayfish when it was in the water, but not as
residue on rice
the
crayfish ate. Scientists applied a seed treatment to the rice according to the label.28 Other
aquatic animals that are very
sensitive
to
chlorantraniliprole include
water fleas (Daphnia)29,30 and
freshwater
midges
called chironomids.31
Chlorantraniliprole
affected how
fast midge larvae grew into adults when
tested at levels found in the environment.32
ECOTOXICOLOGY
CLASSIFICATION -
CHLORANTRANILIPROLE4 |
|
High Toxicity |
Moderate Toxicity |
Low Toxicity |
Very Low Toxicity |
Avian (single dose) Oral LD50 |
≤ 50 mg/kg |
> 51-500 mg/kg |
> 5000 mg/kg |
Fish LC50 |
≤ 1 mg/L |
> 1-10 mg/L |
> 10–100 mg/L |
> 100 mg/L |
Aquatic Invertebrate LD50 |
≤ 1 mg/L |
> 1-10 mg/L |
> 10–100 mg/L |
> 100 mg/L |
HONEYBEE
RATINGS4 |
|
High Toxicity |
Moderate Toxicity |
Low Toxicity |
Honeybee (direct contact or oral exposure) Acute
LD50 |
≤ 2 μg/bee |
> 2-11 μg/bee |
> 11 μg/bee |
The shaded boxes reflect the effects to birds, fish, and other wildlife
mentioned in this
fact
sheet.
Modeled after the U.S. Environmental Protection Agency, Office of Pesticide
Programs,
Ecotoxicity
Categories for Terrestrial and Aquatic Organisms.
https://www.epa.gov/pesticide-science-andassessing-
pesticide-risks/technical-overview-ecological-risk-assessment-0
You may be wondering why the "High Toxicity" column has
smaller numbers than
the
"Low Toxicity"
column. This is because if a smaller amount of the pesticide caused a health
effect, it's
more
toxic. If it takes a larger amount of the pesticide to cause a health
effect, it's less
toxic.
|
For more detailed information about chlorantraniliprole please visit the list of referenced
resources below, call the National Pesticide Information Center, Monday - Friday, 8:00am -
12:00pm
Pacific Time (11:00am - 3:00pm Eastern Time) at 800-858-7378, or visit us on the web at
npic.orst.edu. NPIC
provides
objective,
science-based answers to questions
about pesticides.
- Chlorantraniliprole Compound Summary; PubChem, National Center for Biotechnology
Information,
National
Library of Medicine, National Institutes of Health, 2021.
- NPIC Product Research Online (NPRO): Chlorantraniliprole; National Pesticide Information
Center,
Corvallis, OR, 2021.
- Hannig, G. T.; Ziegler, M.; Marcon, P. G. Feeding Cessation Effects of Chlorantraniliprole, a New
Anthranilic
Diamide Insecticide, in Comparison with Several Insecticides in Distinct Chemical Classes and
Mode-of-Action
Groups. Pest Manag Sci 2009, 65, 969–974. https://doi.org/10.1002/ps.1781.
- Chlorantraniliprole Pesticide Fact Sheet; US Environmental Protection Agency, Office of
Prevention,
Pesticides and Toxic Substances, U.S. Government Printing Office, 2008.
- Cordova, D.; Benner, E. A.; Sacher, M. D.; Rauh, J. J.; Sopa, J. S.; Lahm, G. P.; Selby, T. P.;
Sevenson, T.
M.;
Flexner, L.; Gutteridge, S.; Rhoades, D. F.; Wu, L.; Smith, R. M.; Tao, Y. Anthranilic Diamides: A New
Class
of
Insecticides with a
Novel Mode of Action, Ryanodine Receptor Activation. Pestic Biochem PhysPestic Biochem
Phys
2006, 84, 196–214.
- Sattelle, D. B.; Cordova, D.; Cheek, T. R. Insect Ryanodine Receptors: Molecular Targets for Novel Pest
Control
Chemicals. Invert Neurosci 2008, 8, 107–119.
- Final Human Health and Ecological Risk Assessment for Chlorantraniliprole Rangeland Grasshopper
and
Mormon
Cricket Suppression Applications; US Department of Agriculture, Marketing and Regulatory
Programs,
Animal and Plant Health Inspection Service, 2019.
- Brugger, K. E.; Xole, P. G.; Newman, I. C.; Parker, N.; Scholz, B.; Suvagia, P.; Walker, G.; Hammond, T.
G.
Selectivity of Chlorantraniliprole to Parasitoid Wasps. Pest Manag Sci 2010, 66,
1075–1081.
- Krishnan, N.; Zhang, Y.; Aust, M. E.; Hellmich, R. L; Coats, J. R.; Bradbury, S. P. Monarch Butterfly
(Danaus
Plexippus) Life‐Stage Risks from Foliar and Seed‐Treatment Insecticides. Envir Tox
Chem 2021,
40
(6), 1761–1777.
- Pepper, B. P.; Carruth, L. A. A New Plant Insecticide for Control of the European Corn Borer. J
Econ
Entomol 1945, 38 (1), 59–66.
- Chlorantraniliprole: Human Health Risk Assessment for Proposed Uses on Oilseeds and
Soybean;
US
Environmental Protection Agency Office of Prevention, Pesticides and Toxic Substances, US Government
Printing
Office, 2012.
- Marsala, R. Z.; Capri, E.; Russo, E.; Bisagni, M.; Colla, R.; Lucini, L.; Gallo, A.; Suciu, N. A. First
Evaluation of Pesticides Occurrence in Groundwater of Tidone Valley, an Area with Intensive Viticulture.
Sci
Total Envir 2020, 736 (139730).
- Mishra, A. K.; Chandiraseharan, V. K.; Jose, N.; Suarsanam, T. D. Chlorantraniliprole: An Unusual
Insecticide
Poisoning in Humans. Indian J Crit Care Med 2016, 20 (12), 742–744.
- Conclusion on the Peer Review of the Pesticide Risk Assessment of the Active Substance
Chlorantraniliprole.
EFSA Journal 2013, 11 (6), 3143. https://doi.org/10.2903/j.efsa.2013.3143.
- Abdel-Mobdy, Y. E.; Moustafa, M. A. M.; Nahas, A. H. A.; Abdel-Rhaman, H. R. Sub-Acute and Sub-Chronic
Effect of
Chlorantraniliprole (Coragen® 20% SC) on Albino Rat. J Plant Prot and Pathol, Mansoura
University
2017, 8
(6), 297–303.
- Chlorantraniliprole: Problem Formulation for Registration Review; US Environmental
Protection
Agency,
Office of Chemical Safety and Pollution Prevention, U.S. Government Printing Office, 2020.
- He, M.; Jia, H. C.; Zheng, Y. Concentration and Dissipation of Chlorantraniliprole and Thiamethoxam
Residues
in
Maize Straw, Maize, and Soil. J Envir Sci Health B 2016, 51 (9), 594–601.
- Zhang, J-M.; Chai, W-G.; Wub, Y-L. Residues of Chlorantraniliprole in Rice Field Ecosystem.
Chemosphere
2012, 87, 132–136.
- Lavtizar, V.; van Gestel, C. A. M.; Dolenc, D.; Trebse, P. Chemical and Photochemical Degradation of
Chlorantraniliprole and Characterization of Its Transformation Products. Chemosphere 2014,
95,
408–414.
- Sun, C.; Bei, K.; Xu, Y.; Pan, Z. Effect of Biochar on the Degradation Dynamics of Chlorantraniliprole
and
Acetochlor in Brassica Chinensis L. and Soil under Field Conditions. ACS Omega 2021, 6,
217–226.
- Wang, T-T.; Cheng, J.; Liu, X-J.; Jiang, W.; Zhang, C-L.; Xu, X-Y. Effect of Biochar Amendment on the
Bioavailability of Pesticide Chlorantraniliprole in Soil to Earthworm. Ecotoxicol Envir
Saf
2012, 83,
96–101.
- Larson, J. L.; Redmond, C. T.; Potter, D. A. Comparative Impact of an Anthranilic Diamide and Other
Insecticidal
Chemistries on Beneficial Invertebrates and Ecosystem Services in Turfgrass. Pest Manag
Sci
2012, 68,
740–748.
- Larson, J. L.; Redmond, C. T.; Potter, D. A. Impacts of a Neonicotinoid, Neonicotinoid-Pyrethroid
Premix,
and
Anthranilic Diamide Insecticide on Four Species of Turf-Inhabiting Beneficial Insects.
Ecotoxicol
2014,
23, 252–259.
- Martinou, A. F.; Seraphides, N.; Stavrinides, M. C. Lethal and Behavioral Effects of Pesticides on the
Insect
Predator Macrolophus Pygmaeus. Chemosphere 2014, 96, 167–173.
- Gradish, A. E.; Scott-Dupree, C. D.; Shipp, L.; Harris, C. R.; Ferguson, G. Effect of Reduced Risk
Pesticides
for Use in Greenhouse Vegetable Production on Bombus Impatiens (Hymenoptera: Apidae).
Pest
Manag
Sci 2010, 66, 142–146.
- Liu, T.; Wang, X.; Chen, D.; Li, Y.; Wang, F. Growth, Reproduction and Biochemical Toxicity of
Chlorantraniliprole in Soil on Earthworms (Eisenia Fetida). Ecotoxicol Environ
Saf
2018, 150,
18–25.
- Lavtizar, V.; Berggren, K.; Trebse, P.; Kraak, M. S.; Verweij, R. A.; van Gestel, C. A. M. Comparative
Ecotoxicity of Chlorantraniliprole to Non-Target Soil Invertebrates. Chemosphere 2016,
159,
473–479.
- Barbee, G. C.; McClain, W. R.; Lanka, S. K.; Stout, M. J. Acute Toxicity of Chlorantraniliprole to
Non-Target
Crayfish (Procambus Clarkii) Associated with Rice-Crayfish Cropping Systems. Pest
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- Lavtizar, V.; Helmus, R.; Kools, S. A. E.; Dolenc, D.; van Gestel, C. A. M.; Trebse, P.; Waaijers, S.
L.;
Kraak,
M. H. S. Daphnid Life Cycle Responses to the Insecticide Chlorantraniliprole and Its Transformation
Products.
Environ Sci Technol 2015, 49, 3922–3929.
- Cui, F.; Chai, T.; Qian, L.; Wang, C. Effects of Three Diamides (Chlorantraniliprole, Cyantraniliprole
and
Flubendiamide) on Life History, Embryonic Development and Oxidative Stress Biomarkers of Daphnia
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- Rodrigues, A. C. M.; Gravato, C.; Quintaneiro, C.; Golovko, O.; Žlábek, V.; Barata, C.; Soares, A. M. V.
M.;
Pestana, J. L. T. Life History and Biochemical Effects of Chlorantraniliprole on Chironomus
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Sci Total Envir 2015, 508, 506–513.
- Maloney, E. M.; Sykes, H.; Morrissey, C.; Peru, K. M.; Headley, J. V.; Libera, K. Comparing the Acute
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NPIC fact sheets are designed to answer questions
that
are
commonly
asked by the general public about pesticides that are regulated by the
U.S. Environmental Protection Agency (US EPA). This document is
intended to be educational in nature and helpful to consumers for
making decisions about pesticide use.