Ractopamine hydrochloride |
![]() Last updated: 16/09/2025 |
![]() |
(Also known as: ractopamine HCl) |
|
![]() |
|
A substance often used as a feed additive to promote performance. Now banned in many countries including the EU & china. | |
---|---|---|
|
Once used for its economic and performance benefits - increasing rate of body mass gain, improving feed efficiency, and increasing carcass leanness | |
|
Pigs; Cattle; Turkeys |
Approval status |
|
Not approved | |
---|---|---|
|
Not approved |
Chemical structure |
|
The technical material is a mixture of 4 stereoisomers. It is the RR-form of ractopamine is the most biologically active isomer. | |
---|---|---|
|
C₁₈H₂₄ClNO₃ | |
|
CC(CCC1=CC=C(C=C1)O)NCC(C2=CC=C(C=C2)O)O.Cl | |
|
- | |
|
JHGSLSLUFMZUMK-UHFFFAOYSA-N | |
|
InChI=1S/C18H23NO3.ClH/c1-13(2-3-14-4-8-16(20)9-5-14)19-12-18(22)15-6-10-17(21)11-7-15;/h4-11,13,18-22H,2-3,12H2,1H3;1H | |
|
Yes |
General status |
|
Feed additive; Animal growth promotor | |
---|---|---|
|
Phenethanolamine | |
|
- | |
|
- | |
|
Synthetic | |
|
A phenolethanolamine beta-adrenoceptor agonist | |
|
[Beta-adrenergic receptor, Agonist] | |
|
90274-24-1 | |
|
415-170-5 | |
|
- | |
|
- | |
|
14010333 | |
|
- | |
|
None allocated | |
|
No | |
|
Banned in the EU & UK | |
|
337.8 | |
|
- | |
|
4-[3-[[2-hydroxy-2-(4-hydroxyphenyl)ethyl]amino]butyl]phenol;hydrochloride | |
|
- | |
|
- | |
|
- | |
|
- | |
|
- | |
|
Commercial |
|
|
|||
---|---|---|---|---|
|
Current; Banned in many countries | |||
|
1980s, discovered; 1999, first approvals USA | |||
|
|
|||
|
|
|||
|
Typically formulated as a Type A medicated substance which is a concentrated premix designed to be incorporated into animal feed | |||
|
The commercial production of ractopamine hydrochloride typically begins with the synthesis of its core structure via reductive amination, using precursors like raspberry ketone and octopamine. Under controlled conditions, these compounds undergo microwave-assisted hydrogenation in the presence of heterogeneous catalysts such as platinum or rhodium on carbon, which significantly accelerates the reaction and improves selectivity toward the desired beta-adrenergic agonist. Once the ractopamine free base is formed, it is purified and then crystallised to achieve high purity. The final step involves acidification with hydrochloric acid, converting the free base into its hydrochloride salt. | |||
|
Published GHG data is not available for most pharmaceuticals. However, according to industry, global averages suggest producing 1 kg of a typical active pharmaceutical ingredient can range from 10 to 100 kg CO₂e for small molecule drugs and potentially up to 1000 kg CO₂e for complex biologicals such as vaccines, depending on the drug type, its formulation, complexity of synthesis, solvent recovery, and energy sources used. |
|
![]() |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
31000 | F3 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 ) 3 = Unverified data of known source |
High | ||||||||
|
- | - | - | ||||||||
|
163.9 | F3 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 ) 3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
- | |||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
Max absorbance at 225.8nm=463 and 277.6nm=93 | F3 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 ) 3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
Substance may enter the environment via the urine of treated animals or by leaching from spilt medicated feed. |
Degradation |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
|
1.1 | F3 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 ) 3 = Unverified data of known source |
Non-persistent | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
0.009 | F3 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 ) 3 = Unverified data of known source |
Non-persistent | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
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 |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
|
26.7 | F3 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 ) 3 = Unverified data of known source |
Slightly mobile | |||||||
|
2265 | ||||||||||
|
USEPA data: Kd range 14.5-36.0 mL g⁻¹, Koc range 2007-2698 mL g⁻¹, Soils=3 | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
- | ||||||||||
|
- |
Fate indices |
|
|
|
|
||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
0.03 | Calculated | Low leachability | ||||||||||||||||||||||||||
|
|
6.3 | F3 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 ) 3 = Unverified data of known source |
Low potential | |||||||||||||||||||||||||
|
- | - |
Known metabolites |
None
|
![]() |
Terrestrial ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | |||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
- | |||||||||||
|
- | - | - | ||||||||
- | |||||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - |
Aquatic ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
5.44 | P3 P = Other non-EU, UK or US Governments and Regulators Lepomis macrochirus3 = Unverified data of known source |
Moderate | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
34.5 | F3 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 ) Daphnia magna3 = Unverified data of known source |
Low | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
> 101.2 | P4 P = Other non-EU, UK or US Governments and Regulators Raphidocelis subcapitata4 = Verified data |
Low | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - |
|
- | - | - | |||
|
- | - | - |
|
![]() |
General |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
> 2.8 | P3 P = Other non-EU, UK or US Governments and Regulators Rat 4 hr3 = Unverified data of known source |
- | ||||||||
|
Intraperitoneal LD₅₀ = 367 mg kg⁻¹ | F3 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 ) Rat3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | |||||||||
|
- | ||||||||||
|
Rapidly emininated via the urine | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
- |
Health issues |
|
|
||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
May cause skeletal muscle tremors and behavioural changes May cause cardiovascular effects |
Handling issues |
|
|
|||
---|---|---|---|---|
|
Not compatible with oxidising agents Will produce irritating and toxic gases if heated to decomposition Corrosive |
|||
|
- | |||
|
Not listed (Not listed) | |||
|
- | |||
|
- | |||
|
- |
|
![]() |
|
|
||
---|---|---|---|
|
ractopamine hydrochloride | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- |
Record last updated: | 16/09/2025 |
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 |