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CAS 106-46-7

1,4-Dichlorobenzene (p-Dichlorobenzene)

carcinogenVOCHAPindoor air pollutantOSHA carcinogen

p-Dichlorobenzene is the chemical that makes modern mothballs and solid air fresheners smell the way they do. It is one of the most common indoor air pollutants in American homes — measurable in the blood of 96% of Americans tested — and it is a probable liver carcinogen.

Where It Comes From

Para-dichlorobenzene (p-DCB) was developed as an alternative to naphthalene mothballs beginning in the 1940s and became the dominant mothball formulation in the US [1]. Its strong characteristic odor — described as similar to old urinal cakes — also made it popular as a deodorizer for toilet bowls, urinal blocks, and room air fresheners. By the 1990s it was used in millions of American homes and was detectable in the blood of nearly every American sampled in CDC biomonitoring studies [2]. p-DCB is also used as a chemical intermediate in pesticide and pharmaceutical production. Industrial sources include its manufacture and use in dye synthesis, pharmaceutical production, and as a fumigant for soil and stored products. Like other chlorinated aromatics, it is volatile and persistent, accumulating in indoor air from products and in body fat from dietary exposure [3].

How You Are Exposed

Household use of p-DCB mothballs and solid air fresheners is the most universal exposure pathway — these products are designed to sublimate into the air, which is precisely what makes them release p-DCB into indoor air [1]. In homes using these products, indoor air concentrations can significantly exceed outdoor air. The chemical also accumulates in carpets, fabric, and furniture in rooms where products are used. CDC's National Biomonitoring Program found 2,5-dichlorophenol (a p-DCB metabolite) in 96% of Americans tested, reflecting essentially universal background exposure [2]. Dietary exposure occurs through contaminated water and food. Drinking water contamination near production facilities and industrial discharge points is documented. Occupational exposure in chemical manufacturing and dye production can be significant [3].

Why It Matters

p-DCB is classified as a possible human carcinogen (IARC Group 2B), with clear evidence for liver and kidney tumors in animal studies and suggestive human evidence for non-Hodgkin lymphoma [1]. It accumulates in fatty tissues and is slow to be eliminated from the body. The liver and kidney are primary targets of chronic toxicity — p-DCB causes hepatotoxicity (elevated liver enzymes, fatty liver) and nephrotoxicity (protein in urine, kidney cell damage) in exposed animals and at high occupational exposures in humans [2]. The central nervous system is affected at higher exposures: headache, fatigue, and neurological symptoms are reported in people with heavy home exposure to p-DCB from mothballs or air fresheners used in enclosed spaces. Chronic indoor use in enclosed rooms creates exposures far higher than background [3].

Who Is at Risk

People who use p-DCB mothballs or solid room deodorizers in enclosed spaces — particularly in small bedrooms, closets, or bathrooms without adequate ventilation — face the highest indoor exposures [1]. Infants and toddlers in rooms where p-DCB products are used breathe a higher proportion of room air per body weight. Workers in p-DCB production, dye manufacture, and pharmaceutical synthesis face occupational exposures [2]. Frequent users of public toilet facilities with urinal blocks are exposed in the short term.

How to Lower Your Exposure

Replace p-DCB mothballs and room deodorizers with safer alternatives: cedar chips, lavender sachets, sealed clothing storage, good ventilation, and baking soda for odor control accomplish the same goals without the carcinogen [1]. If you currently use p-DCB products, remove them, ventilate the space thoroughly, and air out stored items. Never use mothballs in living spaces, bedrooms, or areas accessible to children [2]. Look for toilet deodorizer products labeled "free of paradichlorobenzene" — alternatives exist. Check cleaning product labels for dichlorobenzene. In workplaces, use engineering controls and local exhaust ventilation for any process involving p-DCB [3].

References

  1. [1]IARC. Dichlorobenzenes. IARC Monographs Vol 73. 1999. https://monographs.iarc.who.int/
  2. [2]Sexton K, et al. Evaluating NHANES biomonitoring data for volatile organic compounds. Environ Sci Technol. 2006;40(3):631-7.
  3. [3]ATSDR. Toxicological Profile for Dichlorobenzenes. https://www.atsdr.cdc.gov/toxprofiles/tp10.pdf
  4. [4]CDC. Fourth National Report on Human Exposure to Environmental Chemicals. https://www.cdc.gov/exposurereport/

Recovery & Clinical Information

Body Half-Life

1,4-DCB is fat-soluble and distributes into adipose tissue, with a reported blood half-life of approximately 10-14 days [1]. It is metabolized to 2,5-dichlorophenol (2,5-DCP), which is the urinary biomarker detected in NHANES studies and excreted within days of exposure [2].

Testing & Biomarkers

Urinary 2,5-dichlorophenol (2,5-DCP) is the biomarker of choice and is measured in CDC NHANES — the U.S. geometric mean is approximately 40 µg/g creatinine, reflecting widespread background exposure from moth balls and deodorizers [1]. People who use para-dichlorobenzene mothballs or toilet deodorizers routinely have levels 5-50x the background average [2]. A 24-hour urine collection at an occupational health or environmental medicine clinic can quantify 2,5-DCP. Blood 1,4-DCB can be measured in specialty labs for recent acute exposure [1].

Interventions

The primary intervention is elimination of para-dichlorobenzene-based products from your home: replace mothball blocks and toilet bowl deodorizers with non-DCB alternatives (cedar blocks and chips, lavender sachets, and good moisture control prevent moths naturally) [1]. Ventilate stored spaces rather than using chemical deodorizers. Once source products are removed, urinary 2,5-DCP levels fall dramatically within days to weeks [2]. There is no specific chelation treatment. Liver health support is relevant given 1,4-DCB's hepatotoxic potential [1].

Recovery Timeline

After removing mothball and deodorizer sources, urinary 2,5-DCP levels can fall by 90% within 2-4 weeks — 1,4-DCB exposure is unusual in that the source is so identifiable and removable that body burden is highly controllable [1]. Blood 1,4-DCB levels normalize within days to weeks [2]. For occupational chemical workers, respiratory effects and blood cell changes from chronic high-level exposure resolve within weeks to months after stopping exposure [1].

Recovery References

  1. [1]Heudorf U et al. (2009). Urinary para-dichlorobenzene in the German population. International Journal of Hygiene and Environmental Health. https://doi.org/10.1016/j.ijheh.2008.06.001
  2. [2]ATSDR (2006). Toxicological Profile for 1,4-Dichlorobenzene. https://www.atsdr.cdc.gov/toxprofiles/tp10.pdf

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