As of 2011, NPIC stopped creating technical pesticide fact sheets. The old collection of technical fact sheets will remain available in this archive, but they may contain out-of-date material. NPIC no longer has the capacity to consistently update them. To visit our general fact sheets, click here. For up-to-date technical fact sheets, please visit the Environmental Protection Agency’s webpage.
Molecular Structure -
Paradichlorobenzene
Laboratory Testing: Before pesticides are registered by
the U.S. EPA, they must undergo laboratory testing for
short-term (acute) and long-term (chronic) health effects.
Laboratory animals are purposely given high enough doses
to cause toxic effects. These tests help scientists judge how
these chemicals might affect humans, domestic animals,
and wildlife in cases of overexposure.
- Paradichlorobenzene is a chlorinated aromatic hydrocarbon compound used as a fumigant insecticide and repellant.1 The
International Union of Pure and Applied Chemistry (IUPAC) name for paradichlorobenzene is 1,4-dichlorobenzene. The
Chemical Abstracts Service (CAS) registry number is 106-46-7.1
- Paradichlorobenzene was first registered for use in the United States by the United States Department of Agriculture
(USDA) in 1947.1 See the text box on Laboratory Testing.
- There are three forms of dichlorobenzene, differing in the position
of the two chlorine atoms on the benzene ring. 1,2-dichlorobenzene
and 1,3-dichlorobenzene have been used to manufacture
herbicides in addition to other products. 1,4-dichlorobenzene
(paradichlorobenzene) is used as an insecticide.2 This fact sheet
will address the para form unless otherwise noted.
- Paradichlorobenzene is a colorless to white solid crystal with a strong pungent
odor.2,3 It will sublimate, turning from a solid directly into a gas, at room temperatures.3
The average sublimation rate over 19 days at 21-24 °C was 1.6-4.6 x 10-3 g/minute.4
Humans can detect paradichlorobenzene at airborne concentrations of 15 ppm.5
- Vapor pressure3: 4 x 10-1 mmHg at 20 °C
- Octanol-Water Partition Coefficient (log Kow) (unitless)6: 3.52
- Henry's constant (atm·m3/mol)2,6: 1.74 x 10-3 to 2.63 x 10-3
- Molecular weight (g/mol)6: C6H4Cl2 = 147.0
- Solubility (water)6: 0.08 g/L (80 mg/L) at 25 °C
- Soil Sorption Coefficient (Koc) (unitless)2: 275 to 833 depending on soil type
- Paradichlorobenzene is primarily used in mothballs and similar products to protect
clothing from moths.1 Uses for individual paradichlorobenzene products vary
widely. Always read and follow the label when applying pesticide products.
- Paradichlorobenzene is also used in deodorant blocks for rest room toilets and trash containers.2
- Signal words for products containing paradichlorobenzene may range from Caution to Danger. The signal word reflects the combined
toxicity of the active ingredient and other ingredients in the product. See the pesticide label on the product and refer to
the NPIC fact sheets on Signal Words and Inert or "Other" Ingredients.
- To find a list of products containing paradichlorobenzene which are registered in your state, visit the website
https://npic.orst.edu/reg/state_agencies.html select your state then click on the link for "State Products."
Target Organisms
- Paradichlorobenzene vapor is toxic to insects, molds, mildews, and it acts as a deodorizer.2,3 No information was found on
the precise mode of action of paradichlorobenzene on target organisms.
Non-target Organisms
- The mode of action of paradichlorobenzene on non-target organisms is not precisely known, but may involve the binding
of its oxidative metabolites such as the epoxide to proteins within the cells of mammals. Dichlorophenol, a product
of epoxide hydrolysis, may be involved in nephropathy. Other metabolites such as quinones and hydroquinones may be
responsible for the hepatotoxicity of paradichlorobenzene.3
- Recent work with paradichlorobenzene and human neuroblastoma SH-SY5Y cells in vitro suggested that paradichlorobenzene
can act on the nicotinic acetylcholine receptor and appears to affect neuronal calcium ion homeostasis. Researchers
noted that the concentrations of paradichlorobenzene observed to interfere with calcium homeostasis have been found
in vivo in plasma, adipose, and liver tissues.7
Oral
- The acute oral LD50 of paradichlorobenzene in male rats is 3863 mg/kg for males and 3790 mg/kg for females.8 Based on
these values, paradichlorobenzene is low in toxicity via oral exposure.1 See the text boxes on Toxicity Classification and LD50/LC50.
LD50/LC50: A common
measure of acute toxicity is the lethal dose (LD50) or
lethal concentration (LC50) that causes death (resulting
from a single or limited exposure) in 50 percent of the treated
animals. LD50 is generally expressed as the dose in
milligrams (mg) of chemical per kilogram (kg) of body
weight. LC50 is often expressed as mg of chemical per
volume (e.g., liter (L)) of medium (i.e., air or water) the organism
is exposed to. Chemicals are considered highly toxic when the
LD50/LC50 is small and practically non-toxic
when the value is large. However, the LD50/LC50
does not reflect any effects from long-term exposure (i.e., cancer,
birth defects or reproductive toxicity) that may occur at levels below
those that cause death.
- Paradichlorobenzene appears to be more toxic to mice than rats.
A study using CD-1 mice identified an acute oral LD50 of 533 mg/
kg in males and 710 mg/kg in females.19 Researchers determined
an LD50 of 353.6 mg/kg for female CD-1 mice based on an 8-day
oral exposure.20
Dermal
- The acute LD50 for dermal exposure in rats was estimated to be
greater than 6000 mg/kg for both males and females.8 Paradichlorobenzene
is very low in toxicity via dermal exposure.1
- Paradichlorobenzene exposure in eye tissue led to conjunctivitis
and corneal opacity in rabbits. Signs required up to 13 days
to resolve following exposure. Based on total irritation scores, paradichlorobenzene was considered by the U.S. EPA to be
a mild eye irritant.1,9
- Rabbits whose skin was exposed to paradichlorobenzene developed moderate to severe erythema, which persisted for 48
to 72 hours. Paradichlorobenzene is of low toxicity as a skin irritant.1,10
- Based on studies with guinea pigs, paradichlorobenzene is not a skin sensitizer.1,11
Inhalation
- The LC50 for acute inhalation exposure in rats was found to be greater than 6.0 mg/L, which was the highest exposure
concentration that could be attained.12 The U.S. EPA considered paradichlorobenzene to be of low toxicity via inhalation
exposure.1
Signs of Toxicity - Animals
- Companion animals who have eaten mothballs have suffered kidney and liver damage. Behavioral signs include abdominal
pain, vomiting, seizures and tremors.13
- Birds exposed to paradichlorobenzene vapors may show weakness, head bobbing, anorexia, and depression.14 Signs of
exposure in birds following ingestion of contaminated food or paradichlorobenzene itself include weight loss, immunosuppression,
hepatitis, diarrhea, tremors, and seizures.15
TOXICITY CLASSIFICATION - PARADICHLOROBENZENE |
|
High Toxicity |
Moderate Toxicity |
Low Toxicity |
Very Low Toxicity |
Acute Oral LD50 |
Up to and including 50 mg/kg (≤ 50 mg/kg)
| Greater than 50 through 500 mg/kg (>50-500 mg/kg) |
Greater than 500 through 5000 mg/kg (>500-5000 mg/kg) |
Greater than 5000 mg/kg (>5000 mg/kg) |
Inhalation LC50 |
Up to and including 0.05 mg/L (≤0.05 mg/L) |
Greater than 0.05 through 0.5 mg/L (>0.05-0.5 mg/L) |
Greater than 0.5 through 2.0 mg/L (>0.5-2.0 mg/L) |
Greater than 2.0 mg/L (>2.0 mg/L) |
Dermal LD50 |
Up to and including 200 mg/kg (≤200 mg/kg) |
Greater than 200 through 2000 mg/kg (>200-2000 mg/kg) |
Greater than 2000 through 5000 mg/kg (>2000-5000 mg/kg) |
Greater than 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 highlighted boxes reflect the values in the "Acute Toxicity" section of this fact sheet. Modeled after the U.S. Environmental Protection Agency, Office of Pesticide Programs, Label Review Manual, Chapter 7: Precautionary Labeling. https://www.epa.gov/sites/default/files/2018-04/documents/chap-07-mar-2018.pdf |
Signs of Toxicity - Humans
- Paradichlorobenzene may be slightly irritating to the eyes and nasal passages if the vapor is inhaled.16 It can cause a burning
sensation to the skin after prolonged contact.5
- Exposures in the workplace and in the home to high concentrations of paradichlorobenzene have resulted in fatigue,
headache, nausea, vomiting, and weight loss. Other signs were ataxia, loss of coordination, weakness in arms and legs,
slurred speech, and reduced reflexes.17,18
- A pregnant woman who ingested one or two paradichlorobenzene toilet air-freshener blocks per week for the first 38
weeks of her pregnancy developed refractory anemia with red blood cell damage and Heinz body formation. Symptoms
included dizziness, swelling of the ankles, fatigue, and mild anorexia.19
- Acute hemolytic anemia has been reported following ingestion of moth crystals containing paradichlorobenzene.20
- A 69-year-old man developed allergic purpura (skin discoloration) after sitting in a chair treated with paradichlorobenzene
crystals. The patient also developed acute glomerulonephritis.21
- Always follow label instructions and take steps to minimize exposure. If any exposure occurs, be sure to follow the First Aid
instructions on the product label carefully. For additional treatment advice, contact the Poison Control Center at 1-800-
222-1222. If you wish to discuss an incident with the National Pesticide Information Center, please call 1-800-858-7378.
Animals
- Male and female rabbits, rats, and guinea pigs were exposed to 798 ppm paradichlorobenzene vapor for eight hours a
day, five days a week for up to 69 days of exposure. Four of 16 rabbits, 2 of 23 guinea pigs, and 4 of 34 rats died during the
exposure interval at unspecified times. Signs in exposed animals included weight loss, weakness, unkempt appearance,and tremors.
Livers of treated animals exhibited central necrosis, and the kidneys of female rats exhibited swelling in the tubular epithelium.5
- Mice and rats were exposed to paradichlorobenzene vapor at 25, 55, 120, 270, and 600 ppm for 6 hours a day, five days a
week for 13 weeks.22 Researchers observed liver hypertrophy in male rats and mice at the two highest doses, and in female
rats and mice at the highest dose. Female mice exposed to 600 ppm paradichlorobenzene developed increases in mean
blood cell hemoglobin. Male rats and mice in the 600 ppm exposure group developed significantly increased blood urea
nitrogen, an indicator of muscle, blood, and protein breakdown. Male rats developed renal lesions and signs of nephropathy
following exposure to 270 and 600 ppm paradichlorobenzene.22 The hepatoxicity of paradichlorobenzene was found
to be greater in mice than in rats.22
- Researchers exposed 20 male rats, eight male guinea pigs, and eight female guinea pigs to 341 ppm paradichlorobenzene
vapor for seven hours a day, five days a week, for six months. Some male guinea pigs exhibited fatty degeneration, cirrhosis,
and focal necrosis in their livers. Exposed male guinea pigs also grew more slowly than control animals. The kidneys and
livers of exposed male rats were heavier on average than the kidneys and livers of control animals.5
- Researchers also exposed five male and five female rats, five female and five male guinea pigs, and one male and one female
rabbit to 173 ppm paradichlorobenzene vapor for seven hours a day, five days a week, for 16 days. None of the treated
animals died, nor was their growth impaired relative to control animals. Liver and kidneys were heavier in exposed rats,
and spleen weight in exposed male guinea pigs declined relative to control animals. Edema and alveolar hemorrhage were
noted in the lungs of male rats, female guinea pigs and the female rabbit.5
- Ten male and female rats, 10 male mice, eight male and female guinea pigs, one male and female rabbit, and one female
monkey were exposed to paradichlorobenzene vapor at concentrations of 158 ppm for 157 to 219 days. Liver weights of
all exposed rats, female guinea pigs, and the kidney weights of exposed male rats increased. Exposed guinea pigs exhibited
reduced growth rates compared to control animals.5
- Researchers dosed groups of two young male rats with either 10, 100, or 500 mg/kg paradichlorobenzene by gavage five
days a week for four weeks. The highest dose produced swelling in the renal tubular epithelium, and necrosis and swelling
in the liver lobules. No adverse effects were noted in the lower dose groups.5
- Researchers dosed 10 young female rats each with 18.8, 188, or 376 mg/kg paradichlorobenzene by gavage for five days a
week, for a total of 138 doses in 192 days. Slight increases in the mean weight of the liver and kidneys occurred at the two
highest dose rates, and the highest dose group also exhibited reduced spleen mass and focal necrosis and cirrhosis in the
liver. No effects were observed in the low-dose group.5
Humans
- Workers at a manufacturing plant were exposed to up to 550 ppm of paradichlorobenzene in the course of their work.
Workers were exposed eight hours a day, five days a week, for employment durations ranging from eight months to 25
years. No hematological effects or eye damage such as cataracts were noted during medical examinations.5 See the text
box on Exposure.
- A 32-year-old woman reported consuming at least one paradichlorobenzene mothball per day for two years. Signs included
dementia, difficulty speaking, ataxia (lack of coordination), hyperreflexia, distal limb weakness, and skin scaling. Blood
plasma contained 34 μg/ml paradichlorobenzene.23
- Twin girls aged 18 years were hospitalized after sniffing paradichlorobenzene mothballs daily for 5-10 minutes per day for
a few weeks in the case of one twin and 4-6 months in the other. Signs included intracranial hyptertension, unsteady gait,
urinary retention, and neurological symptoms. Total recovery occurred after three and six months, respectively.24
Exposure: Effects of paradichlorobenzene on human health and the environment depend on how much
paradichlorobenzene is present and the length and frequency of exposure. Effects also depend on the health
of a person and/or certain environmental factors.
- Researchers evaluated paradichlorobenzene's endocrine-disrupting potential using a yeast estrogen screen. Following
nine days of incubation, paradichlorobenzene treatment caused dose-dependent increases in β-galactosidase production
similar to 17β-estradiol, a human estrogen hormone.25
- In the same study, adult male and female zebrafish (Danio rerio) were exposed to 10, 18, 32, or 56 mg/L paradichlorobenzene
for 96 hours. Other fish were exposed to 0.32, 1.0, 3.2, 10.0, or 32.0 mg/L 17α-ethynylestradiol (EE2), which was used
as a positive control.25 Researchers estimated that paradichlorobenzene had a relative potency of 2.2 x 10-7
relative to 17β-estradiol.25
- Researchers exposed other adult male and female zebrafish to 1.0, 3.2, 10, and 32 mg/L paradichlorobenzene or 5, 10, 50, or
100 ng/L EE2 as a positive control for 2 weeks.25 Fish exposed to EE2 or 32 mg/L paradichlorobenzene exhibited edema in
their peritoneal cavities and lacked developed gonads and intact eggs.25 Fish exposed to 10 or 32 mg/L paradichlorobenzene
and all dose levels of EE2 also had significantly reduced gonad weight relative to overall body weight.25
Animals
- The National Toxicology Program concluded that there was "clear evidence of carcinogenicity" in male rats and both male
and female B6C3F1 mice following gavage exposure to paradichlorobenzene.26
- Paradichlorobenzene appears to induce liver tumors through stimulation of precancerous lesions, via a mitogenic mode of
action. Researchers concluded that paradichlorobenzene does not appear to be DNA reactive, genotoxic, or mutagenic.27
- Paradichlorobenzene's carcinogenic potential may result from inhibition of cell apoptosis. It does not appear to result from
a genotoxic mechanism.28
- Researchers exposed groups of 50 male rats, 50 female rats, 50 male mice and 50 female mice per dose to paradichlorobenzene
via inhalation exposure for six hours a day, five days a week, for two years. Treatment concentrations were 20, 75, or
300 ppm. Increased rates of liver cancers were noted in both sexes of mice exposed to 300 ppm paradichlorobenzene. No
increased rates of tumor formation were noted in any of the rat treatment groups. Nasal lesions were considered the most
sensitive endpoint following exposure.29
- In a two-year study conducted by the National Toxicology Program, mice were dosed with 300 or 600 mg/kg paradichlorobenzene
by gavage five days a week for 103 weeks. Treated mice of both sexes developed non-neoplastic liver lesions
and kidney abnormalities at greater rates than control mice. Liver cancers (hepatocellular neoplasms) increased in a dosedependent
manner in both sexes of exposed mice.26
- F344/N rats were dosed with 150 or 300 mg/kg paradichlorobenzene by gavage five days a week for 103 weeks as part of
the National Toxicology Program's assessment. Male rats developed kidney cancers (renal tubular cell adenocarcinomas) at
dose-dependent rates. No such renal neoplasms were seen in female rats.26 Adult male rats form the protein á2u-globulin,
which appears to have a major role in onset of nephropathy.30
Humans
- The Health Effects Division (HED) Cancer Assessment Review Committee (CARC) of the U.S. EPA has classified paradichlorobenzene
as not likely to be carcinogenic to humans.1 See the text box on Cancer.
Cancer: Government agencies in the United States and abroad have developed programs to evaluate the
potential for a chemical to cause cancer. Testing guidelines and classification systems vary. To learn more
about the meaning of various cancer classification descriptors listed in this fact sheet, please visit the
appropriate reference, or call NPIC.
- The International Agency for Research on Cancer (IARC) of the World Health Organization concluded that paradichlorobenzene
is possibly carcinogenic to humans, classifying it into Group 2B. The conclusion was based on greater incidences of
liver tumors in exposed mice, and a suggested mechanism of carcinogenicity that could plausibly occur in humans.31
Animals
- Rats and rabbits inhaled 50, 200, or 600 ppm for an unspecified period of time. At the two highest doses, food consumption
and maternal body weight gain declined. Young born to animals dosed with 600 ppm displayed delayed cervical ossification.32
- Rabbits inhaled paradichlorobenzene vapors at 100, 300, or 800 ppm for an unspecified period of time. No teratogenic effects
were noted, but mother rabbits in the highest dose group gained less weight than controls. Development of one of
the major arteries on the aorta was altered in young born to the rabbits in the 800 ppm dose group.33
- Researchers performed a two-generation reproductive study on rats, exposing both males and females to 50, 150 or 450
ppm paradichlorobenzene vapor for an unspecified period of time. The high-dose group produced fewer live pups that
weighed less and had greater mortality rates during the first four days following birth. Male rats showed evidence of nephropathy
in the lowest-dose group, although this was considered an effect that is unique to male rats due to their physiology.34
Humans
- A woman who ingested one or two toilet air freshener blocks per week made of paradichlorobenzene for the first 38 weeks
of her pregnancy gave birth to a normal baby girl. No blood abnormalities were found in either the mother or the child at
the time of delivery although the mother suffered from anemia at the time of hospital admission at 38 weeks.19
Absorption
- Paradichlorobenzene is absorbed rapidly through the lungs and gastrointestinal tract. Researchers demonstrated that
absorption of paradichlorobenzene is more rapid via the oral route than by inhalation in mice. Absorption rates may also
vary by species.3
- Seven human volunteers inhaled paradichlorobenzene at concentrations of 2.4-2.8 ppm for one hour. Researchers estimated
that 46-67% of the inhaled paradichlorobenzene was absorbed by the lungs.35
- Dermal absorption of paradichlorobenzene is slow.3
Distribution
- Paradichlorobenzene residues have been found in human blood, fat, and breast milk.36,37,38 The metabolite 2,5-dichlorophenol
(DCP) has been found in human urine.36
- Distribution varied by gender in rats exposed to paradichlorobenzene vapor at concentrations of 500 ppm for 24 hours.
Male rats had significantly lower concentrations of paradichlorobenzene in their livers than females, whereas females had
significantly lower concentrations in their kidneys. Concentrations peaked at 3 hours following termination of the exposure
period and declined to very low levels by 24 hours post-exposure in both organs for both genders.30
- Researchers exposed female rats via inhalation exposure to paradichlorobenzene for 10 days at 1000 ppm for three hours
per day. Tissue concentrations peaked at six days of exposure. At that time, the greatest concentrations were found in the
fat, with 597 ppm paradichlorobenzene detected. Much lower concentrations were present in the kidneys (43 ppm) and
liver (28 ppm). Blood plasma, muscle and lungs contained maximum concentrations of 19, 7 and 11 ppm paradichlorobenzene,
respectively.39
- Fischer 344 rats were orally dosed with paradichlorobenzene at concentrations of either 100 or 1000 mg/kg in a single
exposure.40 Blood plasma concentrations of paradichlorobenzene and its metabolite 2,5-dichlorophenol fell below detectable
limits one day after exposure in the low-dose group. Four days after exposure, only traces of 2,5-dichlorophenol were
detected in blood plasma in the high-dose group.40 Paradichlorobenzene and 2,5-dichlorophenol were not detected in
adipose and liver tissue four days post-dose, although the kidney still had traces of 2,5-dichlorophenol.40
- Researchers fed paradichlorobenzene to Fischer 344 rats at concentrations of 100 or 1000 ppm for 28 days. Animals were
then given clean food for an additional seven days.40 No paradichlorobenzene or its metabolites were detected in the lowdose
group. Blood plasma levels peaked at day three then declined rapidly, presumably because of enzyme induction.40
Adipose, liver, and kidney tissue residues showed similar patterns, and no traces of paradichlorobenzene or 2,5-dichlorophenol
were detected at day 35.40
- Researchers exposed Wistar rats to paradichlorobenzene vapors at concentrations of 75 or 500 ppm (450 and 3000 mg/
m3) for five hours a day, five days a week, for 18 months. Rats were sacrificed and necropsied at six months, 18 months (the
termination of exposure), and six months after the exposure ended.40 Paradichlorobenzene was found at trace levels in
the plasma of the high-dose group after six months of exposure.40 At six months, 2,5-DCP was measured at concentrations
proportional to the dose of paradichlorobenzene, but concentrations were much reduced at 18 months in the high-dose
group.
- In the study above, adipose tissue concentrations of paradichlorobenzene changed between six to 18 months of exposure.
Changing tissue concentrations varied by sex. In the low-dose group, males had lower levels of paradichlorobenzene in
adipose tissue than females, and in the high-dose group, females had lower levels than males. In both dose groups and
both sexes, levels in the adipose tissue decreased over time. The livers of low-dose animals contained traces of paradichlorobenzene
and 2,5-DCP at 6 months but no detectable traces after 18 months. The livers from the high-dose group also
contained greater concentrations of paradichlorobenzene and 2,5-DCP at six months than at 18 months. All liver concentrations
were below 6 μg/g.40
Metabolism
- The main metabolite of paradichlorobenzene in humans is 2,5-dichlorophenol, but 2,5-dichlorohydroquinone, 2,5-dichlorophenylmethyl
sulfide, 2,5-dichlorophenylmethyl sulfoxide, 2,5-dichlorophenylmethyl sulfone and mercapturic acid derivatives
have also been detected in urine.35
- Adult male Wistar rats dosed with 10, 50, or 250 mg/kg paradichlorobenzene by gavage excreted the sulfate and glucuronide
forms of 2,5-dichlorophenol in their urine. These metabolites accounted for 70% of the dose.41 Mercapturic acid compounds
derived from glutathione conjugates accounted for 10% of the original dose. 2,5-dichlorophenol was also detected.41
- Rats were dosed orally via gavage with radio-labeled paradichlorobenzene at 900 mg/kg. After 72 hours, major metabolites
detected were 2,5-dichlorophenol in the form of sulfide and gulcuronide conjugates.42 No sex-specific differences were
noted.42
- Researchers exposed male and female Fischer 344 rats to 150 or 600 mg/kg paradichlorobenzene by gavage once a day for
up to 28 days.40 Phase I enzymes P450 CYPA1, CYP2B1, and CYP2D1 were induced, reaching maximum levels on day nine.
Enzyme levels in female livers were greater than in male livers.40 The enzymes CYP2B1, CYP3A1, and CYP3A4 were induced in
female rats but not in males.40 The phase II enzymes epoxide hydrolase and glutathione S-transferase peaked at day
nine, but only the high-dose groups showed substantial induction. Induction of phase II enzymes occurred more strongly
in male rat livers than in females. Enzyme induction in the kidneys was much lower than in the liver.40
Excretion
- Human volunteers who inhaled 2.4-2.8 ppm paradichlorobenzene exhaled 0.9-1.4 ppm paradichlorobenzene during the
exposure period of one hour. Exhaled paradichlorobenzene dropped below the detection limit of 0.02 ppm within 10
minutes of the end of exposure.35
- In the same study, the volunteer subjects excreted 4.8-16.2% of the absorbed dose of paradichlorobenzene as 2,5-dichlorophenol
in their urine within 10 hours of the end of the one-hour exposure.35 Blood serum concentrations of paradichlorobenzene
dropped by at least 50% during the first hour post-exposure.35
- Adult male Wistar rats were dosed with 10, 50, or 250 mg/kg of paradichlorobenzene by gavage. Some of the rats were first
pre-treated with isoniazid to induce cytochrome P450 2E1 activity. Clearance rates and half-lives of paradichlorobenzene
were not dose-dependent. Rats with induced enzyme activity had greater clearance rates and reduced blood half-lives of
paradichlorobenzene. The half-life of paradichlorobenzene in blood ranged from 7.06 to 8.12 hours.41 Eighty percent of
the radiolabeled dose was excreted in urine and 4% was excreted in feces. Urinary excretion was enhanced by cytochrome
P450 2E1 induction. Bile was a minor elimination pathway, accounting for 4-30%.41
- In another study, researchers dosed rats orally via gavage with radio-labeled paradichlorobenzene at 900 mg/kg. After 72
hours, male rats had excreted 41.3% and females 37.8% of the radio label in their urine.42
- Biomarkers of exposure to paradichlorobenzene and its metabolite 2,5-dichlorophenol have been reported in the scientific
literature. Scientists have used a purge and trap apparatus followed by gas chromatography and mass spectrometry to
detect and quantify paradichlorobenzene in blood.36,43 Capillary gas chromatography and mass spectrometry have been
used to quantify 2,5-dichlorophenol in urine.36,44,45 These methods of testing for exposure to paradichlorobenzene and its
metabolites have not been well-studied in humans, and the clinical significance is currently unknown.46
- Researchers analyzed urine or blood from 1,000 adults throughout the United States as part of the third National Health
and Nutrition Examination Survey. They detected 2,5-dichlorophenol, the major metabolite of paradichlorobenzene, in
98% of urine and 96% of blood samples evaluated.36
- Paradichlorobenzene was detected in the blood of 41-89% of children tested during four separate monitoring sessions
involving a total of 134 children in the third National Health and Nutrition Examination Survey.47 In another study, the metabolite
2,5-dichlorophenol was found in the urine of 96% of the 197 children tested, at median concentrations of 9 μg/g
and a maximum of 1200 μg/g.48
Soil
- Volatilization is considered the dominant pathway of removal for paradichlorobenzene in soil. Much less of the compound
is removed via photolysis, hydrolysis, oxidation, or biodegradation.2
- Proposed breakdown products for any paradichlorobenzene that does not volatilize include 1,4-dichlorobenzene dihydrodiol,
2,5-dichloro-cis,cis-muconic acid, 2-chloromaleyl-acetic acid, and 2-chloroaceto-acrylic acid.2
- Half-lives of paradichlorobenzene in soil are increased if conditions do not favor volatilization.2 See the text box on Halflife.
- Researchers spiked sandy loam soil with either sewage sludge or a
mixed standardized solution of chlorobenzene compounds. Samples
were taken at 0, 0.6, 1.6, 3.6, 7.6, 18, 32, 67, 147, and 259 days.49 Volatilization
was responsible for most of the losses of chlorobenzenes
from soil.49 The overall half-lives were estimated to be 22.1 days for
sewage-amended soil and 11.2 days for soil spiked with chlorobenzenes.49 The authors cautioned that laboratory conditions likely reduced
soil half-life compared to likely field conditions.49
- A species of Pseudomonas bacteria isolated from sewage sludge
metabolized paradichlorobenzene to 3,6-dichloro-cis-1,2-dihydroxycyclohexa-
3,5-diene, and then to 3,6-dichlorocatechol. This in turn
was metabolized to 2,5-dichloro-cis, cis-muconate. This species of
Pseudomonas was able to draw all of its energy and carbon requirements
from paradichlorobenzene.50
The "half-life" is the time required for half of the
compound to break down in the environment.
1 half-life = 50% remaining
2 half-lives = 25% remaining
3 half-lives = 12% remaining
4 half-lives = 6% remaining
5 half-lives = 3% remaining
Half-lives can vary widely based on environmental
factors. The amount of chemical remaining after a
half-life will always depend on the amount of the
chemical originally applied. It should be noted that
some chemicals may degrade into compounds of
toxicological significance.
Water
- Researchers concluded from measurements of paradichlorobenzene in the waters of Lake Zurich that losses to the atmosphere
accounted for the majority of elimination from the lake system.51
- Adsorption to aquatic sediments may be a dominant fate process in some systems and may decrease volatilization. Biodegradation
may occur under aerobic conditions.52 Paradichlorobenzene does not appear to be broken down by bacteria
under anoxic conditions.53 Photolysis, oxidation, and hydrolysis do not appear to be major processes of degradation for
paradichlorobenzene in water.52
- Under aerobic conditions, biofilm that had been previously exposed to paradichlorobenzene for 10 days eliminated 98%
of the chemical.54
- Paradichlorobenzene has been detected in a small percentage of samples of drinking water, surface water, and ground
water throughout the United States. Detected concentrations were in the parts per trillion to parts per billion range.2,52,55
- Paradichlorobenzene concentrations in groundwater declined with distance from the source river, but the rate of decline
appeared to be seasonal. Researchers speculated that paradichlorobenzene was more likely to penetrate the aquifer during
periods of anoxic conditions within the aquifer.56
- Municipal wastewaters from six treatment plants in southern California were sampled in July and December in 1975. Concentrations
of paradichlorobenzene ranged from less than 0.4 to 230 μg/L.57 Researchers estimated that 4,680 kg/yr paradichlorobenzene
were released from outfall zones. Sediments collected 2 km down-current from outfall zones contained
less than 0.019 mg/kg dry weight paradichlorobenzene.57
Air
- Paradichlorobenzene sublimes at room temperatures, transforming from a solid directly into a gas.2
- Paradichlorobenzene appears to be broken down primarily by interaction with hydroxyl radicals in the atmosphere. The
reaction rate has been reported as 3.2-4.9 x 10-13 cm3/mol-sec.58 The half-life of paradichlorobenzene in the atmosphere
has been estimated at 31 days.52
- Paradichlorobenzene has been detected in rainwater during storms at concentrations of 3.3-7.0 ng/L at ground level in a
residential neighborhood of Portland, Oregon.59
Plants
- Carrots were grown in planters containing one of four soil treatments. Soil was amended with either low (6.35 g/kg dry
weight) or high (59.5 g/kg dry weight) concentrations of sewage sludge containing paradichlorobenzene or spiked with
paradichlorobenzene alone at 59.5 g/kg dry weight.60 Carrot foliage from plants grown in control soil, spiked soil, low sewage
sludge, and high sewage sludge treatments contained 13 ± 1.2 (mean ± SD), 17 ± 4.0, 22 ± 0.43, and 49 ± 3.9 μg/kg
paradichlorobenzene per dry weight of soil.60 Detected levels of paradichlorobenzene in carrot roots ranged from 5.8 μg/
kg to 9.6 μg/kg from treated and untreated soils. Researchers hypothesized that foliar uptake of volatilized paradichlorobenzene
could have been an important pathway.60
- Samples of Chinese cabbages, carrots, celery, radishes, and spinach were obtained from three sites near an urban area in
China. Researchers also collected soil from each site.61 Paradichlorobenzene was detected in spinach and cabbage stems
and roots, in the leaves and roots of celery, and the roots of radishes. The highest residues were in celery, with 89 μg/kg
paradichlorobenzene in the stems and roots. Researchers did not detect paradichlorobenzene in carrots, and it was present
only in the roots of radishes from one site. Soil samples taken from each of the three sites contained an average of 4-27
μg/kg paradichlorobenzene.61
- The aquatic macrophyte Ceratophyllum demersum was exposed to paradichlorobenzene at concentrations of 0.5, 1, 5, 10
and 20 mg/L for 24 hours. At 10 mg/L, researchers observed increases in soluble glutathione S-transferase, glutathione reductase
activity, and glutathione peroxidase activities. The researchers speculated that C. demersum biotransformed paradichlorobenzene
via conjugation to glutathione, and that adverse oxidative effects could occur from paradichlorobenzene
exposure.62
Indoor
- Reported mean concentrations of paradichlorobenzene in indoor air have ranged from 0.65 μg/m3 to 30 μg/m3 and may
be affected by sampling method, indoor environmental conditions and other factors.63,64,65
- Indoor concentrations of paradichlorobenzene were reported from bathrooms and bedrooms where deodorizers and
moth flakes containing paradichlorobenzene were used. Reported concentrations inside closets treated with moth flakes
ranged from 219 to 545 ppb. Concentrations outside of the closets where moth flakes were used ranged from 10.3 to 71.0
ppb. In bathrooms where paradichlorobenzene deodorizers were used, detected concentrations ranged from 78 to 220
ppb.4
- Emission rates of paradichlorobenzene from commercial moth repellents varied even in products of similar size and shape,
although emission rates increased exponentially with increases in ambient temperature. Steady-state concentrations of
paradichlorobenzene in four styles of clothing storage containers were reached at the end of the first week, but the concentration
of paradichlorobenzene retained in the containers varied widely, as did the amount of paradichlorobenzene
that leaked into ambient air around the storage cases.66
- Clothing stored with paradichlorobenzene mothballs may absorb over 900 μg/g of the chemical after five days depending
on where the clothing is placed relative to the mothballs. Although one hour of airing after removal from the storage
container reduced these residues, about half of the residue remained. Researchers concluded that clothing stored with
paradichlorobenzene could itself be a source of indoor air contamination.67
Food Residue
- Paradichlorobenzene was detected in a wide range of prepared foods during the U.S. Food and Drug Administration's
(FDA) Total Diet Study, which included analysis of market basket samples from 1991 to 2003. Of the 51 prepared foods
analyzed for paradichlorobenzene, 29 foods had one or more samples with levels above the limit of quantification. Mean
levels of paradichlorobenzene detected ranged from 0.05 ppb (natural cheddar cheese) to 0.0475 ppm (sunflower seeds).
Foods with the three highest maximum levels detected were: popcorn popped in oil (0.292 ppm), salted margarine (0.208
ppm), and roasted, salted sunflower seeds (0.190 ppm).68
- Researchers evaluated fresh vegetables purchased at retail outlets in the United Kingdom for the presence of various
chlorobenzenes. Paradichlorobenzene was detected in 61% (22 of 36) of samples analyzed. Vegetables evaluated included:
carrots, potatoes, cabbages, cauliflowers, lettuces, onions, beans, peas, and tomatoes. Bean seeds (0.717 μg/kg fresh
weight) and tomato peels (0.619 μg/kg fresh weight) had the highest levels detected, whereas bean pods (0.117 μg/kg
fresh weight) and outer lettuce leaves (0.118 μg/kg fresh weight) had the lowest amounts detected.69
- Paradichlorobenzene has been detected in various fish and aquatic organisms consumed by humans. Trout from the U.S.
Great Lakes region had levels of paradichlorobenzene ranging from 1 to 4 ppb.70
- Paradichlorobenzene was detected in the lipid tissue of fish and crabs caught in the Calcasieu River Estuary near the outfall
of industrial facilities near Lake Charles, LA. Levels in catfish ranged from 0.17 to 0.47 μg/g of lipid, depending on the
location caught. Levels of paradichlorobenzene in other fish ranged from 0.24 to 0.90 μg/g of lipid. The highest amount of
paradichlorobenzene detected was in the lipid tissue of blue crabs (Callinectes sapidus) at 2.5 μg/g.71
- Crabs (Charybdis feriatus) contained paradichlorobenzene at concentrations of 0.5, 0.6 and 5.1 μg/kg in the leg meat, body
meat and carapace meat, respectively.72
Birds
- Researchers fed 10 young Peking ducks 0.5% paradichlorobenzene in their diet for 35 days. By the end of day 28, three
ducks had died and the survivors showed decreased growth rates.5
Fish and Aquatic Life
- Researchers exposed rainbow trout (Oncorhyncus mykiss) and zebrafish (Danio rerio) to water treated with paradichlorobenzene.
The 48-hour LC50 for rainbow trout was 1.18 mg/L, and the 48-hour LC50 for zebrafish was 4.25 mg/L.73
- In the same study, researchers exposed a species of green algae (Selenastrum capricornutum) and an aquatic invertebrate
(Daphnia magna) to paradichlorobenzene in water. The 96-hour EC50 for growth inhibition of the algae was 1.6 mg/L, and
the three-hour EC50 for photosynthesis reduction was 5.2 mg/L. For D. magna, the 24-hour immobilization concentration
(IC50) was 1.6 mg/L.73 See the text box on EC50.
EC50: The median effective concentration (EC50) may be
reported for sublethal or ambiguously lethal effects. This
measure is used in tests involving species such as aquatic
invertebrates where death may be difficult to determine.
This term is also used if sublethal events are being
monitored.
Newman, M.C.; Unger, M.A. Fundamentals of Ecotoxicology; CRC Press, LLC.:
Boca Raton, FL, 2003; p 178.
- Sheepshead minnows (Cyprinodon variegates) were exposed
to paradichlorobenzene in water. Mortality was recorded at 24,
48, 72 and 96 hours. The LC50 values ranged from greater than
7.5 to 10.0 ppm for 24-hour tests and 7.2-7.4 ppm for 48- to 96-hour tests.74
- Researchers exposed zebrafish (Danio rerio) to paradichlorobenzene
in 96-hour static exposure tests, and estimated the
acute LC50 to be 22 mg/L.25
- The LC50 of paradichlorobenzene to bluegill sunfish (Lepomis macrochirus) was determined to be 4.5 mg/L for 24 hours and
4.3 mg/L for 96 hours, but some of the paradichlorobenzene was seen to precipitate out of solution.75 This likely led to an
overestimate of the LC50.
- The 96-hour LC50 in fathead minnows (Pimephales promelas) has been reported as 2.85, 30.0, and 33.7 mg/L.76
- Muscle tissue from six Dover sole (species not specified) captured at a site 2 km down-current from the outfall of a municipal
sewage treatment plant contained less than 0.007 mg/kg wet weight paradichlorobenzene. Sediments from the same
site contained less than 0.019 mg/kg dry weight paradichlorobenzene.57
- Lake trout (Salvelinus namaycush) were collected from Lakes Ontario, Superior, and Huron and rainbow trout (Oncorhyncus
mykiss) were collected from Lake Erie. All fish were estimated to be at least four years old and they contained concentrations
of paradichlorobenzene ranging from 1-4 ppb.55
- Juveniles of the marine polychaete worm (genus Neanthes, species unspecified) grew significantly less near a sewage outfall.
Sediments at sampling sites contained a range of contaminants including paradichlorobenzene.77 Subsequent laboratory
studies attempted to replicate the reduced growth rates by exposing juvenile Neanthes to clean sediments spiked
with paradichlorobenzene at concentrations an order of magnitude greater than those measured in the field. Significant
reductions in dry weight were detected only at the highest concentration tested. Researchers speculated that paradichlorobenzene
alone was not responsible for effects observed in the field.76
- The LC50 for juvenile sand crabs (Portunus pelagicus) was estimated to be 5.03 μmol/L.78,79 The EC10 and EC50, defined by the
researchers as concentrations of paradichlorobenzene at which growth rate was reduced by 10% and 50% compared to
controls, was estimated to be 0.44 and 1.37 μmol/L, respectively.79
- Researchers exposed green alga (Ankistrodesmus falcatus) to paradichlorobenzene and estimated the EC50 to be 0.136 mM
paradichlorobenzene. At that concentration, primary productivity of the alga was reduced by 50%.80
Terrestrial Invertebrates
- No information was found regarding the toxicity of paradichlorobenzene to terrestrial invertebrates.
- The Health Effects Division (HED) Cancer Assessment Review Committee (CARC) of the EPA has classified paradichlorobenzene
as not likely to be carcinogenic to humans.1 See the text box on Cancer.
- The concentration of paradichlorobenzene considered Immediately Dangerous to Life and Health (IDLH) is 150 ppm.81
- PEL/TWA: The Permissible Exposure Level for a time-weighted average exposure (PEL TWA) for paradichlorobenzene is 10 ppm.82
- The Maximum Contaminant Level (MCL) for paradichlorobenzene in drinking water is 0.075 mg/L or 75 ppb.83 See the text
box on Maximum Contaminant Level (MCL).
Maximum Contaminant Level (MCL): The MCL is the highest
level of contaminant that is legally allowed in drinking water.
The MCL is enforceable. The MCL is typically measured in
milligrams (mg) of contaminant per liter (L) of water.
U.S. Environmental Protection Agency, National Primary Drinking Water Regulations. https://www.epa.gov/ground-water-and-drinking-water/national-primary-drinking-water-regulations#one
- The Threshold Limit Value-Time Weighted Average (TLV-TWA) is 10 ppm for paradichlorobenzene.2
- The Minimal Risk Level (MRL) for acute inhalation exposure to paradichlorobenzene has been set at 2 ppm.2
Date Reviewed: December 2010
Please cite as: Gervais, J.; Luukinen, B.; Buhl, K.; Stone, D. 2010. Paradichlorobenzene Technical Fact Sheet; National Pesticide
Information Center, Oregon State University Extension Services. https://npic.orst.edu/factsheets/archive/PDBtech.html.