Hexachlorobenzene (Ref: ENT 1719) |

Last updated: 29/01/2025
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(Also known as: HCB; perchlorobenzene) |
Hexachlorobenzene is a fumigant fungicide. It has a low aqueous solubility and is volatile with a low potential for leaching to groundwater. It may be very persistent in soil systems. Hexachlorobenzene las a low mammalian toxicity but a high potential to bioaccumulate. It may also be carcinogenic. It is highly toxic to fish and moderately toxic to birds, aquatic invertebrates, algae and earthworms. |
The following alerts are based on the data in the tables below. An absence of an alert does not imply the substance has no implications for human health, biodiversity or the environment but just that we do not have the data to form a judgement.
Environmental fate |
Ecotoxicity |
Human health |
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An chlorinated hydrocarbon fungicide used to control bunt and a pesticide transformation product |
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Common and Dwarf bunt |
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Wheat and some other cereals |
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- |
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Banned in many countries |
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circa 1947, introduced |
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Not approved |
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Expired |
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No UK approval for use as a pesticide |
EC Regulation 1107/2009 (repealing 91/414) |
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Not approved |
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Not applicable |
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Expired |
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Not applicable |
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Yes |
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ATAustria |
BEBelgium |
BGBulgaria |
CYCyprus |
CZCzech Republic |
DEGermany |
DKDenmark |
EEEstonia |
ELGreece |
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ESSpain |
FIFinland |
FRFrance |
HRCroatia |
HUHungary |
IEIreland |
ITItaly |
LTLithuania |
LULuxembourg |
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LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
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None |
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C₆Cl₆ |
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C1(=C(C(=C(C(=C1Cl)Cl)Cl)Cl)Cl)Cl |
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No data |
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CKAPSXZOOQJIBF-UHFFFAOYSA-N |
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InChI=1S/C6Cl6/c7-1-2(8)4(10)6(12)5(11)3(1)9 |
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Yes |
Cambridge Crystallographic Data Centre diagrams |
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Common Name |
Relationship |
Link |
hexachlorobenzene |
- |
 |
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Fungicide, Metabolite, Other substance |
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Soil |
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Biocide; Wood preservative |
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Organochloride fungicide; Fumigant fungicide |
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- |
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- |
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Synthetic |
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Fumigant action on fungal spores. It affects porphyrin synthesis and consequently the proteins involved in the metabolism and transport of oxygen. |
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118-74-1 |
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204-273-9 |
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161 |
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061001 |
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8370 |
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602-065-00-6 |
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284.80 |
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- |
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perchlorobenzene |
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hexachlorobenzene |
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WFD priority substance; OSPAR candidate; Rotterdam Convention (Class Ia) - subject to PIC regulations |
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EU Directive 2008/105/EC EQS surface waters: annual average 0.01 µg l⁻¹; max measured 0.05 µg l⁻¹ UK Statutory standard for the protection of aquatic life in inland, coastal and territorial waters: 0.03 µg l⁻¹ as annual average Other standards are also available |
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Not applicable |
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Not applicable |
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Not applicable |
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Not known |
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- |
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Colourless crystals |
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- Anticarie
- Bent-cure
- Granero
- No Bunt
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Often used as a seed dressing. |
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0.0047 |
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Low |
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- |
- |
- |
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226 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
- |
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325 |
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- |
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- |
- |
- |
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242 |
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- |
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8.51 X 1003 |
Calculated |
- |
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3.93 |
H4 H = The US ARS pesticide properties database. Dataset is no longer available. 4 = Verified data |
High |
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Soluble |
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- |
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Regulatory data - observed in metabolism and farm animal feeding studies |
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- |
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2.044 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
- |
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- |
- |
- |
- |
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1.45 |
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Low volatility. If applied directly to plants or soil, drift is a concern & mitigation is advisable |
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1.03 X 1001 |
H4 H = The US ARS pesticide properties database. Dataset is no longer available. 4 = Verified data |
Moderately volatile |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
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2000 |
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Very persistent |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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General literature states DT₅₀ range 2.7-7.5 years, highly persistent |
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- |
- |
- |
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- |
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9.7 |
R3 R = Peer reviewed scientific publications 3 = Unverified data of known source |
- |
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Lettuce leaves, n=1 |
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- |
- |
- |
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- |
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- |
- |
- |
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- |
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- |
- |
- |
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- |
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As this parameter is not normally measured directly, a surrogate measure is used: ‘Photochemical oxidative DT₅₀’. Where data is available, this can be found in the Fate Indices section below. |
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- |
Soil adsorption and mobility |
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- |
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Non-mobile |
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50000 |
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- |
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- |
- |
- |
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- |
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- |
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- |
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- |
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-2.31 |
Calculated |
Low leachability |
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5.35 X 10-03 |
Calculated |
- |
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Estimated concentrations of chemicals with Koc values greater than 9995 ml g⁻¹ are beyond the scope of the regression data used in SCI-GROW development. If there are concerns for such chemicals, a higher tier groundwater exposure assessment should be considered, regardless of the concentration returned by SCI-GROW |
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High |
Calculated |
- |
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Non-mobile |
Calculated |
- |
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- |
- |
- |
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35000 |
(Other literature values Log BCF range 1.6-5.4 (R3); PIC DGD gives BCF range 375-35000) |
High potential |
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Not available |
- |
None
Terrestrial ecotoxicology |
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> 10000 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Rat |
Low |
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- |
- |
- |
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- |
- |
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- |
- |
- |
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> 575 |
Colinus virginianus |
Moderate |
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- |
- |
- |
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- |
- |
- |
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> 1000 |
Eisenia foetida |
Low |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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0.03 |
Oncorhynchus mykiss |
High |
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> 0.0048 |
P3 P = Other non-EU, UK or US Governments and Regulators 3 = Unverified data of known source Pimephales promelas 32 day |
High |
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- |
- |
- |
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0.5 |
Daphnia magna 24 hr |
Moderate |
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> 0.003 |
P4 P = Other non-EU, UK or US Governments and Regulators 4 = Verified data Daphnia magna |
High |
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- |
- |
- |
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- |
- |
- |
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- |
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- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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0.01 |
Scenedesmus abundans |
Moderate |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
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HUMAN HEALTH AND PROTECTION |
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High (class III) |
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- |
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> 10000 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Rat |
Low |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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List I |
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- |
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Primary source of exposure is via diet but risk is low as substance is banned |
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Risk via exhalation |
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EU MRL pesticide database |
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- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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Carcinogen |
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Endocrine disruptor |
✓Yes, known to cause a problem |
A0 A = Chromosome aberration (EFSA database) 0 = No data ; B0 B = DNA damage/repair (EFSA database) 0 = No data ; C0 C = Gene mutation (EFSA database) 0 = No data ; D0 D = Genome mutation (EFSA database) 0 = No data ; E3 E = Unspecified genotoxicity type (miscellaneous data source) 3 = Negative |
✓Yes, known to cause a problem |
Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
?Possibly, status not identified |
XNo, known not to cause a problem |
No data found |
Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
No data found |
✓Yes, known to cause a problem |
No data found |
Eye irritant |
Phototoxicant |
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XNo, known not to cause a problem |
No data found |
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Extremely hazardous IARC Group 2B carcinogen; CLP data - known human carcinogen; US NTP - suspected carcinogen; US EPA - probable human carcinogen Endocrine issues - Severely disruption of thyroid hormone production |
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IMDG Transport Hazard Class 6.1 |
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Health: H350, H372 Environment: H400, H410 |
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Ia (Extremely hazardous) |
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UN2729 |
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Packaging Group III (minor danger) |
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- |
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hexachlorobenzene |
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hexachlorobenzène |
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Hexachlorbenzol |
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hexachlorbenzen |
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esaclorobenzene |
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hexaclorobenceno |
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- |
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heksachlorobenzen |
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- |
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- |
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hexachloorbenzeen |
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- |
Record last updated: |
29/01/2025 |
Contact: |
aeru@herts.ac.uk |
Please cite as: |
Lewis, K.A., Tzilivakis, J., Warner, D. and Green, A. (2016) An international database for pesticide risk assessments and management. Human and Ecological Risk Assessment: An International Journal, 22(4), 1050-1064. DOI: 10.1080/10807039.2015.1133242 |