Heptenophos (Ref: OMS 1845) |
![]() Last updated: 15/09/2025 |
![]() |
(Also known as: HOE 02982; AE F002982) |
|
![]() |
|
An obsolerte organophosphate veterinary ectoparasitcide | |
---|---|---|
|
Used to control ticks, lice, mites and fleas | |
|
Farm animals; Domestic pets |
Approval status |
|
Not approved | |
---|---|---|
|
Not approved |
Chemical structure |
|
Heptenophos exhibits chirality, containing two chiral centres, which allows it to exist as a racemic mixture of stereoisomers. | |
---|---|---|
|
C₉H₁₂ClO₄P | |
|
COP(=O)(OC)OC1=C(C2C1CC=C2)Cl | |
|
- | |
|
GBAWQJNHVWMTLU-UHFFFAOYSA-N | |
|
InChI=1S/C9H12ClO4P/c1-12-15(11,13-2)14-9-7-5-3-4-6(7)8(9)10/h3-4,6-7H,5H2,1-2H3 | |
|
Yes |
General status |
|
Ectoparasiticide | |
---|---|---|
|
Organophosphate insecticide; Organophosphate acaricide | |
|
>93 | |
|
- | |
|
Synthetic | |
|
Systemic with stomach, contact and respiratory action. Acetylcholinesterase (AchE) inhibitor. | |
|
[Cholinesterase, Inhibitor] | |
|
23560-59-0 | |
|
245-737-0 | |
|
527 | |
|
215600 | |
|
62773 | |
|
015-126-00-1 | |
|
- | |
|
None allocated | |
|
No | |
|
- | |
|
250.6 | |
|
- | |
|
7-chlorobicyclo[3.2.0]hepta-2,6-dien-6-yl dimethyl phosphate | |
|
7-chlorobicyclo[3.2.0]hepta-2,6-dien-6-yl dimethyl phosphate | |
|
- | |
|
Marine Pollutant | |
|
- | |
|
Light brown liquid |
Commercial |
|
|
|||
---|---|---|---|---|
|
- | |||
|
1971, first reported | |||
|
|
|||
|
|
|||
|
Usually supplied as an emulsifiable concentrate. | |||
|
Heptenophos is produced through a multi-step chemical process involving esterification and dehydration. The synthesis begins with the preparation of a wet crude product, which is mixed with an organic solvent and subjected to distillation and dehydration to isolate heptenophos. This is followed by spray heating or membrane evaporator heating, using the solvent as a carrier to enable continuous dehydration, blending, and packaging. In a final step, complexation with maneb and zinc is performed in the same solvent system, which facilitates crystal transformation while minimizing product decomposition and reducing impurities and dust pollution. | |||
|
Data for the amount of life cycle GHGs produced by heptenophos are not available in the public domain. However, whilst estimates vary, more general data suggests that between 14 and 19 kilograms of CO₂e is emitted per kilogram of insecticide produced. |
|
![]() |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
2200 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
High | ||||||||
|
Miscible | L3 L = Pesticide manuals and hard copy reference books / other sources Acetone3 = Unverified data of known source |
- | ||||||||
Miscible | L3 L = Pesticide manuals and hard copy reference books / other sources Methanol3 = Unverified data of known source |
- | |||||||||
130 | L3 L = Pesticide manuals and hard copy reference books / other sources Hexane3 = Unverified data of known source |
- | |||||||||
1000 | L3 L = Pesticide manuals and hard copy reference books / other sources Xylene3 = Unverified data of known source |
- | |||||||||
|
Not applicable | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
- | ||||||||
|
64 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
152 | L3 L = Pesticide manuals and hard copy reference books / other sources (closed cup)3 = Unverified data of known source |
- | ||||||||
|
|
2.09 X 1002 | Calculated | - | |||||||
|
2.32 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Low | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
1.28 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
- | |||||||||||
|
65 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Highly volatile. If applied directly to plants or soil, drift is a concern & mitigation is advisable | ||||||||
|
5.73 X 10-05 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Non-volatile | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- |
Degradation |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
|
1.4 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Non-persistent | |||||||
|
- | - | - | ||||||||
|
1.4 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
Non-persistent | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
General literature DT₅₀ range 0.07-1.8 days (R3) | ||||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
13 | K4 K = Research datasets (e.g. Pandora, Demetra; these datasets no longer available). Norman Ecotoxicology database. (click here ) 4 = Verified data |
Non-persistent | |||||||
|
- | ||||||||||
|
7 | K4 K = Research datasets (e.g. Pandora, Demetra; these datasets no longer available). Norman Ecotoxicology database. (click here ) 4 = Verified data |
Fast | ||||||||
|
2.1 | K4 K = Research datasets (e.g. Pandora, Demetra; these datasets no longer available). Norman Ecotoxicology database. (click here ) 4 = Verified data |
Moderately fast | ||||||||
|
- | - | - | ||||||||
|
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. | ||||||||||
|
- |
Soil adsorption and mobility |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | N2 N = Various trusts, NGOs & charities data 2 = Unverified data of unknown source |
Moderately mobile | |||||||
|
163 | ||||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
- | ||||||||||
|
- |
Fate indices |
|
|
|
|
||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
0.26 | Calculated | Low leachability | ||||||||||||||||||||||||||
|
|
Low risk | Q3 Q = Miscellaneous data from online sources Based on LogP < 33 = Unverified data of known source |
Low risk | |||||||||||||||||||||||||
|
- | - |
Known metabolites |
None
|
![]() |
Terrestrial ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
96 | F4 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) Rat4 = Verified data |
High | ||||||||
|
|
- | L2 L = Pesticide manuals and hard copy reference books / other sources Rat 2 yr2 = Unverified data of unknown source |
- | |||||||
|
15 | - | |||||||||
|
- | - | - | ||||||||
|
> 17 | L3 L = Pesticide manuals and hard copy reference books / other sources Coturnix japonica3 = Unverified data of known source |
High | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
> 98 | L3 L = Pesticide manuals and hard copy reference books / other sources Eisenia foetida3 = Unverified data of known source |
Moderate | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
|
> 2.19 | R3 R = Peer reviewed scientific publications Bombus terrestris 72 hr3 = Unverified data of known source |
Moderate | |||||||
- | |||||||||||
|
0.53 | R3 R = Peer reviewed scientific publications Bombus terrestris 72 hr3 = Unverified data of known source |
High | ||||||||
- | |||||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
Harmful at dose 340 g ha⁻¹ | AA3 AA = IOBC Database on classification of side effects to beneficial organisms, 2005 Chrysoperla carnea3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
Harmful at dose 340 g ha⁻¹ | AA3 AA = IOBC Database on classification of side effects to beneficial organisms, 2005 Typhlodromus pyri3 = Unverified data of known source |
- | ||||||||
|
- | - | - |
Aquatic ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
0.056 | L3 L = Pesticide manuals and hard copy reference books / other sources Oncorhynchus mykiss3 = Unverified data of known source |
High | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
0.0022 | L3 L = Pesticide manuals and hard copy reference books / other sources Daphnia magna3 = Unverified data of known source |
High | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
35 | K2 K = Research datasets (e.g. Pandora, Demetra; these datasets no longer available). Norman Ecotoxicology database. (click here ) Unknown species2 = Unverified data of unknown source |
Low | ||||||||
|
25.0 | Q2 Q = Miscellaneous data from online sources Unknown species2 = Unverified data of unknown source |
Low | ||||||||
|
|
- | - | - |
|
- | - | - | |||
|
- | - | - |
|
![]() |
General |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
High (class III) | - | - | ||||||||
|
96 | F4 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) Rat4 = Verified data |
High | ||||||||
|
2000 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
- | ||||||||
|
0.95 | L3 L = Pesticide manuals and hard copy reference books / other sources Rat3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
List I; List II | - | - | ||||||||
|
|
- | |||||||||
|
- | ||||||||||
|
Eliminated through hepatic metabolism, followed by renal and faecal excretion | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
- |
Health issues |
|
|
||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
No further information available |
Handling issues |
|
|
|||
---|---|---|---|---|
|
IMDG Transport Hazard Class 6.1 | |||
|
Health: H301 Environment: H400, H410 |
|||
|
Ib (Highly hazardous) | |||
|
UN2810 | |||
|
Packaging Group III (minor danger) | |||
|
- |
|
![]() |
|
|
||
---|---|---|---|
|
heptenophos | ||
|
heptenophos | ||
|
Heptenophos | ||
|
heptenophos | ||
|
eptenofos | ||
|
heptenofos | ||
|
heptenophos | ||
|
heptenofos | ||
|
- | ||
|
- | ||
|
heptenofos | ||
|
- |
Record last updated: | 15/09/2025 |
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 |