According to the
Agency for Toxic Substances and Disease Registry (ATSDR) (2007), benzene is both a synthetically made and naturally occurring chemical from processes that include: volcanic eruptions, wild fires, synthesis of chemicals such as
phenol, production of
synthetic fibers, and fabrication of
rubbers,
lubricants,
pesticides, medications, and
dyes. The major sources of benzene exposure are
tobacco smoke, automobile service stations, exhaust from motor vehicles, and industrial emissions; however, ingestion and dermal absorption of benzene can also occur through contact with contaminated water. Benzene is hepatically metabolized and excreted in the
urine. Measurement of air and water levels of benzene is accomplished through collection via
activated charcoal tubes, which are then analyzed with a
gas chromatograph. The measurement of benzene in humans can be accomplished via
urine,
blood, and
breath tests; however, all of these have their limitations because benzene is rapidly metabolized in the human body. Exposure to benzene may lead progressively to aplastic
anemia,
leukaemia, and
multiple myeloma.
Occupational Safety and Health Administration (OSHA) regulates levels of benzene in the workplace. The maximum allowable amount of benzene in workroom air during an 8-hour workday, 40-hour workweek is 1 ppm. As benzene can cause
cancer,
National Institute for Occupational Safety and Health (NIOSH) recommends that all workers wear special
breathing equipment when they are likely to be exposed to benzene at levels exceeding the recommended (8-hour) exposure limit of 0.1 ppm.
Benzene exposure limits The
United States Environmental Protection Agency has set a
maximum contaminant level for benzene in
drinking water at 0.005 mg/L (5 ppb), as promulgated via the US National Primary Drinking Water Regulations. This regulation is based on preventing benzene
leukemogenesis. The maximum contaminant level goal (
MCLG), a nonenforceable health goal that would allow an adequate margin of safety for the prevention of adverse effects, is zero benzene concentration in drinking water. The EPA requires that spills or accidental releases into the environment of 10 pounds (4.5 kg) or more of benzene be reported. The US
Occupational Safety and Health Administration (OSHA) has set a permissible exposure limit of 1 part of benzene per million parts of air (1 ppm) in the workplace during an 8-hour workday, 40-hour workweek. The short term exposure limit for airborne benzene is 5 ppm for 15 minutes. These legal limits were based on studies demonstrating compelling evidence of health risk to workers exposed to benzene. The risk from exposure to 1 ppm for a working lifetime has been estimated as 5 excess leukemia deaths per 1,000 employees exposed. (This estimate assumes no threshold for benzene's carcinogenic effects.) OSHA has also established an action level of 0.5 ppm to encourage even lower exposures in the workplace. The US
National Institute for Occupational Safety and Health (NIOSH) revised the
Immediately Dangerous to Life and Health (IDLH) concentration for benzene to 500 ppm. The current NIOSH definition for an IDLH condition, as given in the NIOSH Respirator Selection Logic, is one that poses a threat of exposure to airborne contaminants when that exposure is likely to cause death or immediate or delayed permanent adverse health effects or prevent escape from such an environment. In September 1995, NIOSH issued a new policy for developing
recommended exposure limits (RELs) for substances, including carcinogens. As benzene can cause cancer, NIOSH recommends that all workers wear special breathing equipment when they are likely to be exposed to benzene at levels exceeding the REL (10-hour) of 0.1 ppm. The NIOSH short-term exposure limit (STEL – 15 min) is 1 ppm. American Conference of Governmental Industrial Hygienists (ACGIH) adopted Threshold Limit Values (TLVs) for benzene at 0.02 ppm TWA in 2024. Germany’s regulation comes through something called Technische Regeln für Gefahrstoffe which means Germany’s Technical Rule For
Hazardous Substances. The workspace exposure limit in Germany is TRGS 900. Whereas the TRGS 910 sets the level of risk for the chemicals that can cause cancer and explains the amount that should be reduced. When it comes to the
EU exposure limit it’s about 0.66 mg^3. When looking at TRGS 910 according to the numbers from national assessment criteria the target concentration is AC: 0.2 mg/m3 and the temporary upper concentration level is TC: 1.9 mg/m3. Scientific research shows that there is correlation between
leukemia and benzene exposure; average exposure to benzene below 5μg/m^3 lowered the leukemia burden from benzene by nearly a third. This information from the VegAS project shows how trying to control the level of benzene has a lot of importance since it has caused problems in the country. This project was funded by The Federal Ministry of Environment,
Nature Conservation. In terms of the benzene market, Germany is a top 3 producer in the European Union. It is the
BASF that has responsibility when it comes to looking over chemicals such as benzene. Also, Germany is in the top 6 when it comes to the
exports in the world for benzene, same when it comes to
imports. They are the 7th largest importers in the world as well. When looking at the EU, they are one of the largest traders when it comes to benzene.
Toxicology Biomarkers of exposure Several tests can determine exposure to benzene. Benzene itself can be measured in breath, blood, or urine, however such testing is usually limited to the first 24 hours post-exposure due to the relatively rapid removal of the chemical by exhalation or biotransformation. The majority of people in developed countries have measureable baseline levels of benzene and other aromatic petroleum hydrocarbons in their blood. In the body, benzene is enzymatically converted to a series of oxidation products including
muconic acid,
phenylmercapturic acid,
phenol,
catechol,
hydroquinone and
1,2,4-trihydroxybenzene. Most of these metabolites have some value as biomarkers of human exposure, since they accumulate in the urine in proportion to the extent and duration of exposure, and they may still be present for some days after exposure has ceased. The current ACGIH biological exposure limits for occupational exposure are 500 μg/g creatinine for muconic acid and 25 μg/g creatinine for phenylmercapturic acid in an end-of-shift urine specimen.
Biotransformations Even if it is not a common substrate for metabolism, benzene can be oxidized by both
bacteria and
eukaryotes. In bacteria,
dioxygenase enzyme can add an
oxygen to the ring, and the unstable product is immediately reduced (by
NADH) to a cyclic
diol with two double bonds, breaking the aromaticity. Next, the diol is newly reduced by NADH to
catechol. The catechol is then metabolized to
acetyl CoA and
succinyl CoA, used by organisms mainly in the
citric acid cycle for energy production. Human metabolism of benzene is complex and begins in the liver. Several enzymes are involved. These include
cytochrome P450 2E1 (CYP2E1), quinine oxidoreductase (NQ01 or DT-diaphorase or
NAD(P)H dehydrogenase (quinone 1)), GSH, and myeloperoxidase (MPO). CYP2E1 is involved at multiple steps: converting benzene to
oxepin (benzene oxide),
phenol to
hydroquinone, and hydroquinone to both benzenetriol and
catechol. Hydroquinone, benzenetriol and catechol are converted to polyphenols. In the bone marrow, MPO converts these polyphenols to benzoquinones. These intermediates and metabolites induce genotoxicity by multiple mechanisms including inhibition of
topoisomerase II (which maintains chromosome structure), disruption of
microtubules (which maintains cellular structure and organization), generation of oxygen free radicals (unstable species) that may lead to point mutations, increasing oxidative stress, inducing
DNA strand breaks, and altering DNA
methylation (which can affect gene expression). NQ01 and GSH shift metabolism away from toxicity. NQ01 metabolizes
benzoquinone toward
polyphenols (counteracting the effect of MPO). GSH is involved with the formation of
phenylmercapturic acid. Genetic polymorphisms in these enzymes may induce loss of function or gain of function. For example, mutations in CYP2E1 increase activity and result in increased generation of toxic metabolites. NQ01 mutations result in loss of function and may result in decreased detoxification. Myeloperoxidase mutations result in loss of function and may result in decreased generation of toxic metabolites. GSH mutations or deletions result in loss of function and result in decreased detoxification. These genes may be targets for genetic screening for susceptibility to benzene toxicity.
Molecular toxicology The paradigm of toxicological assessment of benzene is shifting towards the domain of molecular toxicology as it allows understanding of fundamental biological mechanisms in a better way.
Glutathione seems to play an important role by protecting against benzene-induced DNA breaks and it is being identified as a new biomarker for exposure and effect. Benzene causes chromosomal aberrations in the peripheral blood leukocytes and bone marrow explaining the higher incidence of leukemia and multiple myeloma caused by chronic exposure. These aberrations can be monitored using
fluorescent in situ hybridization (FISH) with DNA probes to assess the effects of benzene along with the hematological tests as markers of hematotoxicity. Benzene metabolism involves enzymes coded for by polymorphic genes. Studies have shown that genotype at these loci may influence susceptibility to the toxic effects of benzene exposure. Individuals carrying variant of NAD(P)H:quinone oxidoreductase 1 (NQO1), microsomal epoxide hydrolase (EPHX) and deletion of the glutathione S-transferase T1 (GSTT1) showed a greater frequency of DNA single-stranded breaks.
Biological oxidation and carcinogenic activity One way of understanding the carcinogenic effects of benzene is by examining the products of biological oxidation. Pure benzene, for example, oxidizes in the body to produce an epoxide,
benzene oxide, which is not excreted readily and can interact with DNA to produce harmful mutations.
Routes of exposure Inhalation Outdoor air may contain low levels of benzene from automobile service stations, wood smoke, tobacco smoke, the transfer of gasoline, exhaust from motor vehicles, and industrial emissions. About 50% of the entire nationwide (United States) exposure to benzene results from smoking tobacco or from exposure to tobacco smoke. After smoking 32 cigarettes per day, the smoker would take in about 1.8 mg of benzene. This amount is about 10 times the average daily intake of benzene by nonsmokers. Inhaled benzene is primarily expelled unchanged through exhalation. In a human study 16.4 to 41.6% of retained benzene was eliminated through the lungs within five to seven hours after a two- to three-hour exposure to 47 to 110 ppm and only 0.07 to 0.2% of the remaining benzene was excreted unchanged in the urine. After exposure to 63 to 405 mg/m3 of benzene for 1 to 5 hours, 51 to 87% was excreted in the urine as phenol over a period of 23 to 50 hours. In another human study, 30% of absorbed dermally applied benzene, which is primarily metabolized in the liver, was excreted as phenol in the urine.
Exposure from soft drinks Under specific conditions and in the presence of other chemicals
benzoic acid (a preservative) and
ascorbic acid (Vitamin C) may interact to produce benzene. In March 2006, the official
Food Standards Agency in
United Kingdom conducted a survey of 150 brands of soft drinks. It found that four contained benzene levels above
World Health Organization limits. The affected batches were removed from sale. Similar problems were reported by the US Food & Drug Administration.
Contamination of water supply In 2005, the water supply to the city of
Harbin in China with a population of almost nine million people, was cut off because of a major benzene exposure. Benzene leaked into the
Songhua River, which supplies drinking water to the city, after
an explosion at a China National Petroleum Corporation (CNPC) factory in the city of Jilin on 13 November 2005. When plastic water pipes are subject to high heat, the water may be contaminated with benzene.
Genocide Nazi Germany used benzene administered via
injection as one of their many methods for killing. ==See also==