United States
Environmental Protection
Agency	

Prevention, Pesticides
And Toxic Substances
(7505C)	

May 2005

<>EPA New Pesticide Fact Sheet

Picaridin

Description of
the Chemical

Generic Name: 2-(2-hydroxyethyl)-l-piperidinecarboxylic acid 1-methylpropyl
ester

Common Name: Picaridin
Trade Name: KBR 3023

EPA Shaughnessy Code (OPP Chemical Code): 070705

Chemical Abstracts Service (CAS) Number: 119515-38-7

Year of Initial Registration: 2001

Pesticide Type: Insect Repellent

Chemical Family: Piperidines

Manufacturer: Lanxess Corp.

Ill Park West Drive
Pittsburgh, PA 15275-1112

Use Patterns
and Formulations

Application Sites:
Types of Formulation:
Formulation Types
Registered:

Target Pest:
Use Patterns:

Human body

Insect and acarid repellent products only.

96.8% a.i. Technical; 5% & 7% pump sprays; 10%
aerosol spray and 5.15% towelette wipes
There are no combination Picaridin/Sunscreen
products.

Biting flies, mosquitoes, chiggers, ticks, and fleas
Household floors, walls, bathroom and other non-
food contact surfaces.

Science Findings	Summary Statement

Technical grade Picaridin has low acute oral, dermal and inhalation
toxicity. It is classified as Toxicity Category IV for acute inhalation toxicity and
primary dermal irritation and Toxicity Category in for acute oral, acute dermal
and primary eye irritation. It is not a dermal sensitizer. No developmental
toxicity was observed and effects in the offspring were observed only at or above
dosage levels which resulted in evidence of maternal toxicity. Picaridin was not
shown to be mutagenic in a battery of tests. The toxicology data base is complete
and no additional studies are required.

Based on the use pattern, skin applied insect repellent, picaridin is unlikely to
result in measurable exposures to the environment. Under environmental pH and


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temperature conditions, picaridin is stable to hydrolysis, therefore, hydrolysis is
not expected to contribute to degradation of picaridin in the environment.

Chemical
Characteristics

Technical Grade

Molecular Formula:

Ci2H23F9N03

Physical:

Liquid

Color:

Colorless

Odor:

Nearly odorless

Melting Point:

N/A

Molecular Weight:

229.3g/mole

Vapor Pressure:

0.3 kPa(2.25 mm Hg) at 20 C

Octanol-Water



Partition Coefficient



(K-ow):

4.94 (86,000)

Solubility:

In water: insoluble

In 2-propanol: miscible
In ethanol: miscible

Human Health
Assessment

Acute Toxicity

In studies using laboratory animals, Picaridin technical is of relatively low
acute toxicity: Toxicity Category III for acute oral and acute dermal; and Toxicity
Category IV for primary eye and skin irritation. The technical is not a dermal
sensitizer.

[NOTE: For acute oral, dietary, mammalian:

Category I = very highly or highly toxic
Category II = moderately toxic
Category III = slightly toxic
Category IV = practically non-toxic]

TOXICOLOGY CHARACTERISTICS
Technical Grade

The acute toxicity profile table below represents Picaridin technical grade/MUP
based on the following table of study results:

Guideline No.

Study type

Results

Tox







Category

2


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81-1

Acute Oral

Rat: LD50 = 4743 mg/kg in males
Rat: LD50 =2236 mg/kg in males

HI

81-2

Acute Dermal

LD50 >2000 mg/kg (Limit Test)

III

81-3

Acute Inhalation

LC50 >4.364 mg/L.

IV

81-4

Primary Eye Irritation

Moderate ocular irritant

m

81-5

Primary Skin Irritation

Not a dermal irritant

IV

81-6

Dermal Sensitization

not a sensitizer



81-8

Acute Neurotoxicity

NOEL = >2000 mg/kg (HDT)
NOAEL = 2000 mg/kg



Subchronic Toxicity

14-Week Feeding -Rat:

NOAEL = 301 mg/kg/day

LOAEL = 1033 mg/kg/day based on decreased body weight/weight
gain in both sexes, and effects on the male kidneys including
increased relative kidney weights and increased incidence of protein
droplet degenerative nephropathy.

Dermal Subcronic -Rat:

NOAEL (systemic) = 200 mg/kg/day

LOAEL (systemic) = 500 mg/kg/day (slight to minimal diffuse liver
hypertrophy, individual necrotic liver cells, slight hyaline
degeneration in the kidneys, increased incidence of foci of tubular
regeneration, and chronic kidney inflamation)

NOAEL (dermal irritation) = <80 mg/kg/day
LOAEL (dermal irritation) = 80 mg/kg/day (scabs, red foci, and
exfoliation at the dosing site). Complete reversal was seen after a
4-week recovery period.

Dermal Developmental Toxicity - Rat:

NOAEL (maternal) = 400 mg/kg/day (HDT; slight increases in
absolute and relative liver weights; 9% and 5%, respectively.

LOAEL (maternal) >400 mg/kg/day.

NOAEL (developmental) = 400 mg/kg/day (delayed ossification
attributed to maternal stress due to the dermal dosing regimen).
LOAEL (developmental^ 400 mg/kg/day. No developmental
toxicity was observed and effects in the offspring were observed only
at or above dosage levels which resulted in evidence of maternal
toxicity.

Dermal Developmental Toxicity - Rabbit:

NOAEL (systemic) >200 mg/kg/day (HDT)

NOAEL (developmental) >200 mg/kg/day
NOAEL (dermal irritation) = <50 mg/kg/day

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LOAEL (dermal irritation) = 50 mg/kg/day (LDT) No developmental
toxicity was observed.

Dermal Reproductive Toxicity - Rat:

NOEL (systemic) = 200 mg/kg/day

NOAEL (systemic) >200 mg/kg/day

NOEL (reproductive) = 200 mg/kg/day

NOAEL (reproductive) >200 mg/kg/day. No systemic or

reproductive toxicity was found.

Chronic Toxicity and Carcinogenicity

Dermal Chronic Toxicity - Dog:

NOAEL (systemic) = 200 mg/kg/day (HDT)

NOAEL (dermal irritation) = 200 mg/kg/day. No toxicity was

observed.

Dermal Carcinogenicity -Mouse (18 months):

NOEL = 200 mg/kg/day

NOAEL = 200 mg/kg/day. There is no evidence of carcinogenicity.
Dermal Chronic Toxicty/Carcinogenicity - Rat:

NOAEL = 200 mg/kg/day (HDT; liver cystic degeneration with no
corroborating liver weight or clinical pathology anomalies). There is
no evidence of carcinogenicity.

Carcinogenicity.

The Agency determined that Picaridin is not likely to be a human
carcinogen by the dermal route.

Endodrine Disruption:

The Agency found no evidence that Picaridin is an endocrine disruptor.

Dietary Exposure

Because of its use pattern, people are not exposed to residues of Picaridin.

OCCUPATIONAL AND RESIDENTIAL EXPOSURE

Occupational Exposure

Based on Picaridin's residential use pattern, handlers (mixers, loaders, and
applicators) are not exposed to Picaridin.

Residential Exposure

Picaridin generally is of low acute toxicity, and based on the available
toxicological data, the Agency believes that the normal use of Picaridin does not
present a health concern to the general U.S. population (the Agency's human risk


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assessment has identified no toxicologically significant effects in animal studies.)
Picaridin has been classified as not likely to be a human carcinogen.

Because of Picaridin's unusual use pattern (direct application to human
skin), the Agency believes it is prudent to require clear, common sense use
directions and restrictions on Picaridin product labels. These directions include
how to apply and when to reapply, restrictions on how often to apply and
directions for using on children.

Environmental Fate
and Ecological
Effects
Characteristics

Technical Grade

The Agency has reviewed the proposed Section 3 registrations for the use
of Picaridin as an insect repellent. Based on the ecological effects data submitted
by the registrant, the Agency concluded that the product should pose no risks to
terrestrial and aquatic organisms from the proposed use pattern. The use should
provide non-target organisms extremely limited access to the chemical.

ENVIRONMENTAL FATE

Hydrolysis:

Under environmental pH and temperature conditions, Picaridin is
stable to hydrolysis.

ECOLOGICAL EFFECTS
Likelihood of Adverse Effects on Non-Target Organisms
Terrestrial Organism Toxicity

Avian Dietary:	Non-toxic

Bobwhite quail: LC50 >5000 ppm a.i.-diet. Based on the results of
this study, Picaridin can be considered as non-toxic to birds.

Aquatic Organism Toxicity

Freshwater Fish: Moderately Toxic
Rainbow trout: 96-hr LC50= 173 mg/1

Freshwater Invertebrates

Daphnia Magna: Picaridin was tested at five concentrations ranging
from 10 mg/1 to 100 mg/1 at 24 and 48 hours. No effects were found
at any concentration.

Green algae:

Scenedesmus subspicatus: The study was of 72 hour endurance and
included 6 nominal concentrations ranging from 5.6 mg/1 to 100
mg/1. Effects were determined within the range of 56 mg/1 and 100
mg/1. The NOEC and LOEC were determined to be 56 mg/1.

For More	contact person:

Information Joseph M. Tavano Biologist, PM Team 10

Insecticide Branch , Registration Division (7505C)

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Office of Pesticide Programs
U.S. EPA, Ariel Rios Building
1200 Pennsylvania Avenue NW
Washington, DC 20460

Office Location and Telephone Number:

Room 222, Crystal Mall #2
1801 South Bell Street
(703)305-6411

Electronic copies of the this fact sheet are available on the Internet. See
http ://www. epa. gov/ opprdOO 1 /factsheets/

DISCLAIMER: The information in this Pesticide Fact Sheet is for information
only and is not to be used to satisfy data requirements for pesticide registration.
The information is believed to be accurate as of the date on the document.

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