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ACTIVITY:
Acaricide,
Insecticide (pyrethroid)
Structure:
Adverse
Effects:
Ataxia
Body Weight Decrease
CNS
Endocrine:
Suspected Disruptor
Endocrine: Testicular
Eye
Liver
Tremors/Convulsions
Environmental
Rationale
for US EPA to add Cyhalothrin to the Toxic Release Inventory
Cyhalothrin
administered orally (in capsules) to dogs at 10 mg/kg/day
for 26 weeks produced occasional disturbances of the nervous
system (unsteadiness and/or muscular trembling). The NOEL
for these effects was not defined. In a 1-year dog study,
ataxia, muscle tremors, and convulsions were observed following
oral administration at 3.5 mg/kg/day. Abnormal gait and
convulsions were observed at 0.5 mg/kg/day. The LOEL of
the study was 0.5 mg/kg/day and the NOEL was 0.1 mg/kg/day.
EPA believes that there is sufficient evidence for listing
cyhalothrin on EPCRA section 313 pursuant to EPCRA section
313(d)(2)(B) based on the available neurological toxicity
data.
Ref:
USEPA/OPP. Support Document for the Addition of Chemicals
from Federal Insecticide, Fungicide, Rodenticide Act (FIFRA)
Active Ingredients to EPCRA Section 313. U. S. Environmental
Protection Agency, Washington, DC (1993). As
cited by US EPA in: Federal
Register: January 12, 1994. Part
IV. 40 CFR Part 372. Addition of Certain Chemicals; Toxic
Chemical Release Reporting; Community Right-to-Know; Proposed
Rule.
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Ataxia
(click on for all fluorinated pesticides)
Cyhalothrin administered
orally (in capsules) to dogs at 10 mg/kg/day for 26 weeks produced
occasional disturbances of the nervous system (unsteadiness and/or
muscular trembling). The NOEL for these effects was not defined.
In a 1-year dog study, ataxia, muscle
tremors, and convulsions were observed following oral administration
at 3.5 mg/kg/day. Abnormal gait and convulsions were observed
at 0.5 mg/kg/day. The LOEL of the study was 0.5 mg/kg/day and
the NOEL was 0.1 mg/kg/day. EPA believes that there is sufficient
evidence for listing cyhalothrin on EPCRA section 313 pursuant
to EPCRA section 313(d)(2)(B) based on the available neurological
toxicity data.
Ref:
USEPA/OPP. Support Document for the Addition of Chemicals from
Federal Insecticide, Fungicide, Rodenticide Act (FIFRA) Active
Ingredients to EPCRA Section 313. U. S. Environmental Protection
Agency, Washington, DC (1993). As cited by US EPA in: Federal
Register: January 12, 1994. Part IV. 40 CFR Part 372. Addition
of Certain Chemicals; Toxic Chemical Release Reporting; Community
Right-to-Know; Proposed Rule.
Body
Weight Decrease (click
on for all fluorinated pesticides)
-- Cyhalothrin. 13-Week
feeding - rat. 00154805. NOAEL: 2.5 mg/kg/day LOAEL: 12.5
mg/kg/day decreased body weight gain in
males.
-- Cyhalothrin. 28-Day feeding - rat.
00153029. NOAEL: 2 mg/kg/day LOAEL: 10 mg/kg/day
clinical signs of neurotoxicity. At higher doses,
decreases in body weight gain and food consumption
and changes in organ weights.
-- cyhalothrin. 28-Day feeding - rat.
00154806. NOAEL: 1.0 mg/kg/day LOAEL: 2.0 mg/kg/day decreases
in mean body weight gain in females.
-- cyhalothrin. 4-Week feeding - mouse.
43241901. NOAEL: 64.2/77.9 mg/kg/ day LOAEL: 309/294 mg/kg/ day
mortality, 64.2, 309 mg/kg/day clinical signs of toxicity, decreases
in bodyweight gain and food consumption.
changes in hematology and
organ weights, minimal centrilobular hepatocyte enlargement.
-- cyhalothrin. 28-Day feeding - rat.
00153029. NOAEL: 2 mg/kg/day 1984/Acceptable LOAEL: 10 mg/kg/day
nonguideline. clinical signs of 0, 2, 10, 25, 50, 75 mg/ neurotoxicity.
At kg/day. higher doses, decreases
in body weight gain and food consumption
and changes in organ weights.
-- cyhalothrin. 21-Day dermal toxicity
-rabbit.
00154869. NOAEL: 100 mg/kg/day LOAEL: 1,000 mg/kg/day significant
weight loss
-- cyhalothrin. Developmental toxicity -
rat. 00154800. Maternal NOAEL: 10 mg/kg/day. Maternal LOAEL:
15 mg/ kg/day. uncoordinated limbs, reduced
body weight gain and food consumption. Developmental NOAEL: 15
mg/kg/day, the highest dose tested (HDT) Developmental LOAEL:
>15 mg/kg/day
-- cyhalothrin. Developmental toxicity -
rat. 00154801. Maternal NOAEL: 10 mg/kg/day. Maternal LOAEL:
30 mg/ kg/day. reduced body weight gain and food consumption.
Developmental NOAEL: 30 mg/kg/day (HDT) Developmental LOAEL: >30
mg/kg/day
-- cyhalothrin. 3-Generation Reproduction - rat. 00154802. arental/Offspring
NOAEL: 1.5 mg/kg/day. Parental/Offspring LOAEL: 5.0 mg/kg/day.
decreased parental body weight and body weight gain during premating
and gestation periods and reduced pup weight and weight gain during
lactation). Reproductive NOAEL: 5.0 mg/kg/day (HDT).
-- cyhalothrin. Carcinogenicity -
mouse. 00150842. NOAEL: 15 mg/kg/day. LOAEL: 75 mg/kg/day. increased
incidence of piloerection, hunched posture; decreased body weight
gain in males. Not oncogenic under conditions of study. HDT inadequate.
New study not required at this time. [FAN
Note: The study cited was performed in 1984.]
-- cyhalothrin. 00154803.
Chronic/Carcinogenicity - rat. NOAEL: 2.5
mg/kg/day. LOAEL: 12.5 mg/kg/day. decreases in mean body weight.
Not oncogenic under conditions of study.
Ref: Federal Register: September 27, 2002.
Lambda-cyhalothrin; Pesticide Tolerance. Final Rule.
http://www.fluoridealert.org/pesticides/Lambda.Cyhalot.FR.Sept27.02.htm
CNS
(click
on for all fluorinated pesticides)
Rationale
for US EPA to add Cyhalothrin to the Toxic Release Inventory.
Cyhalothrin administered orally (in capsules) to dogs at 10 mg/kg/day
for 26 weeks produced occasional disturbances of the nervous
system (unsteadiness and/or muscular trembling). The NOEL
for these effects was not defined. In a 1-year dog study, ataxia,
muscle tremors, and convulsions were observed following oral administration
at 3.5 mg/kg/day. Abnormal gait and convulsions were observed
at 0.5 mg/kg/day. The LOEL of the study was 0.5 mg/kg/day and
the NOEL was 0.1 mg/kg/day. EPA believes that there is sufficient
evidence for listing cyhalothrin on EPCRA section 313 pursuant
to EPCRA section 313(d)(2)(B) based on the available neurological
toxicity data.
Ref:
USEPA/OPP. Support Document for the Addition of Chemicals from
Federal Insecticide, Fungicide, Rodenticide Act (FIFRA) Active
Ingredients to EPCRA Section 313. U. S. Environmental Protection
Agency, Washington, DC (1993). As cited by US EPA in:
Federal
Register: January 12, 1994. Part IV.
40 CFR Part 372. Addition of Certain Chemicals; Toxic Chemical
Release Reporting; Community Right-to-Know; Proposed Rule.
-- Cyhalothrin. 28-Day
feeding - rat. 00153029. NOAEL: 2 mg/kg/day LOAEL: 10 mg/kg/day
clinical signs of neurotoxicity. At higher doses,
decreases in body weight gain and food consumption and
changes in organ weights.
-- cyhalothrin. 28-Day feeding - rat.
00154806. NOAEL: 1.0 mg/kg/day LOAEL: 2.0 mg/kg/day decreases
in mean body weight gain in females.
-- cyhalothrin. 26-Week feeding - dog.
00154795. NOAEL: 1.0 mg/kg/day LOAEL: 2.5 mg/kg/day increase in
liquid feces. At 10.0 mg/kg/ day, clinical
signs of neurotoxicity.
-- cyhalothrin. 28-Day feeding - rat.
00153029. NOAEL: 2 mg/kg/day 1984/Acceptable LOAEL: 10 mg/kg/day
nonguideline. clinical signs of 0, 2, 10, 25, 50, 75 mg/ neurotoxicity.
At kg/day. higher doses, decreases in body
weight gain and food consumption and changes in organ weights.
-- cyhalothrin. Developmental toxicity -
rat. 00154800. Maternal NOAEL: 10 mg/kg/day. Maternal LOAEL:
15 mg/ kg/day. uncoordinated limbs, reduced
body weight gain and food consumption. Developmental NOAEL:
15 mg/kg/day, the highest dose tested (HDT) Developmental LOAEL:
>15 mg/kg/day
Ref: Federal Register: September 27, 2002.
Lambda-cyhalothrin; Pesticide Tolerance. Final Rule.
http://www.fluoridealert.org/pesticides/Lambda.Cyhalot.FR.Sept27.02.htm
Endocrine:
Suspected Disruptor
(click
on for all fluorinated pesticides)
Suspected
Endocrine Disruptor
Ref: PAN
Pesticides Database
Endocrine:
Testicular
(click
on for all fluorinated pesticides)
The physical and behavioral
effects of cyhalothrin were studied in rats. Pregnant Wistar rats
were administered 0 or 0.018% cyhalothrin topically throughout
pregnancy. After delivery the neonates were monitored for development
of fur, testes descent, and ear, eye, and vaginal opening. Body
weights were recorded on postnatal days 2, 7, 14, and 21. The
effects on locomotor activity and inhibitory avoidance behavior
were evaluated on postnatal days 21 and 90. The number of head
dips occurring in a hole board test was recorded on postnatal
day 90. Development of fur and times to testes
descent and ear and eye opening were significantly
delayed in cyhalothrin exposed pups. Time to vaginal opening
was not affected. Body wt of cyhalothrin exposed pups were significantly
increased at postnatal days 2, 7, and 14, but not at postnatal
day 21. Cyhalothrin did not significantly affect locomotor activity
or inhibitory avoidance behavior. Cyhalothrin exposed rats had
a significantly smaller number of head dips in the hole board
test. The authors conclude that prenatal exposure to cyhalothrin
delays development of fur, eye and ear opening, and testes
descent and affects motivational behavior. The delays induced
in fur development and eye and ear opening suggest that cyhalothrin
interferes with maternal or neonatal epidermal growth factor activity.
The delay in testes descent suggests
that prenatal cyhalothrin exposure
induces changes in male sexual development.
[da Silva Gomes M et al; Vet Human Toxicol 33 (4): 315-7 (1991)]
Ref: TOXNET profile from Hazardous Substances
Data Base for Cyhalothrin.
http://www.fluoridealert.org/pesticides/Cyhalothrin.TOXNET.HSDB.htm
Eye
(click
on for all fluorinated pesticides)
The physical and behavioral
effects of cyhalothrin were studied in rats. Pregnant Wistar rats
were administered 0 or 0.018% cyhalothrin topically throughout
pregnancy. After delivery the neonates were monitored for development
of fur, testes descent, and ear, eye, and vaginal opening... The
authors conclude that prenatal exposure to cyhalothrin delays
development of fur, eye and ear opening,
and testes descent and affects motivational behavior. The delays
induced in fur development and eye
and ear opening suggest that cyhalothrin interferes with maternal
or neonatal epidermal growth factor activity. The delay in testes
descent suggests that prenatal cyhalothrin exposure induces changes
in male sexual development. [da Silva Gomes M et al; Vet Human
Toxicol 33 (4): 315-7 (1991)]
Ref: TOXNET profile from Hazardous Substances
Data Base for Cyhalothrin.
http://www.fluoridealert.org/pesticides/Cyhalothrin.TOXNET.HSDB.htm
Liver
(click
on for all fluorinated pesticides)
Long
term toxicity and carcinogenicity Target / critical effect: Liver
Lowest relevant NOAEL: NOEL 1.7 mg/kg bw/d, 2 y rat (cyhalothrin)
Carcinogenicity: Negative
Ref:
European Commission. Review report for the active substance lambda-cyhalothrin.
Finalised in the Standing Committee on Plant Health at its meeting
on 19 October 2000 in view of the inclusion of lambda-cyhalothrin
in Annex I of Directive 91/414/EEC. 7572/VI/97-final. 25 January
2001.
http://europa.eu.int/comm/food/fs/ph_ps/pro/eva/existing/list1-24_en.pdf
Tremors/Convulsions
(click on for all fluorinated
pesticides)
Cyhalothrin administered
orally (in capsules) to dogs at 10 mg/kg/day for 26 weeks produced
occasional disturbances of the nervous system (unsteadiness and/or
muscular trembling). The NOEL for these effects was not defined.
In a 1-year dog study, ataxia, muscle
tremors, and convulsions were observed following oral administration
at 3.5 mg/kg/day. Abnormal gait and convulsions
were observed at 0.5 mg/kg/day. The LOEL of the study was 0.5
mg/kg/day and the NOEL was 0.1 mg/kg/day. EPA believes that there
is sufficient evidence for listing cyhalothrin on EPCRA section
313 pursuant to EPCRA section 313(d)(2)(B) based on the available
neurological toxicity data.
Ref:
USEPA/OPP. Support Document for the Addition of Chemicals from
Federal Insecticide, Fungicide, Rodenticide Act (FIFRA) Active
Ingredients to EPCRA Section 313. U. S. Environmental Protection
Agency, Washington, DC (1993). As cited by US EPA in: Federal
Register: January 12, 1994. Part IV. 40 CFR Part 372. Addition
of Certain Chemicals; Toxic Chemical Release Reporting; Community
Right-to-Know; Proposed Rule.
Environmental
(click
on for all fluorinated pesticides)
Highly
toxic to fish, aquatic invertebrates and honeybees.
"Cyhalothrin and lambda-cyhalothrin
are very toxic to fish in clean water under laboratory conditions.
The available data, summarized in Table 6, demonstrate a
similar high acute toxicity for both cold and warm water
species of fish... Cyhalothrin and lambda-cyhalothrin have
been shown to be toxic to honey-bees
(Apis mellifera) in laboratory tests (Table 10)."
Ref: ENVIRONMENTAL HEALTH
CRITERIA 99: International Programme on Chemical Safety
http://www.inchem.org/documents/ehc/ehc/ehc99.htm#SubSectionNumber:6.2.2
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