Efrotomycin (Ref: FR-02A) |
![]() Last updated: 08/09/2025 |
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(Also known as: Antibiotic FR 02A; mocimycin; MK 621) |
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Efrotomycin is produced by Streptomyces lactamodurans NRRL 3802 and used in veterinary medicine as a narrow-spectrum antibiotic | |
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Mainly used as a growth promoter | |
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Pigs |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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Efrotomycin exhibits geometric (cis-trans) and stereoisomerism, which are crucial to its biological activity. As a complex macrolide antibiotic derived from Streptomyces lactamodurans, its molecular structure includes multiple double bonds with defined E/Z (trans/cis) configurations, as well as several chiral centres that contribute to its isomeric diversity. | |
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C₅₉H₈₈N₂O₂₀ | |
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CCC(C(=O)NCC=CC=C(C)C(C(C)C1C(C(C(O1)C=CC=CC=C(C)C(=C2C(=O)C=CN(C2=O)C)O)O)O)OC)C3(C(C(C(C(O3)C=CC=CC)(C)C)OC4C(C(C(C(O4)C)OC5C(C(C(C(O5)C)OC)O)OC)OC)O)O)O | |
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CCC(C(=O)NC/C=C/C=C(\C)/C(C(C)C1C(C(C(O1)/C=C/C=C/C=C(\C)/C(=C\2/C(=O)C=CN(C2=O)C)/O)O)O)OC)C3(C(C(C(C(O3)/C=C/C=C/C)(C)C)OC4C(C(C(C(O4)C)OC5C(C(C(C(O5)C)OC)O)OC)OC)O)O)O | |
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ZLECMEJICSWJLT-LIWMBINXSA-N | |
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InChI=1S/C59H88N2O20/c1-15-17-19-27-39-58(8,9)53(80-56-45(67)50(74-13)49(35(7)76-56)79-57-51(75-14)44(66)48(73-12)34(6)77-57)52(68)59(71,81-39)36(16-2)54(69)60-29-23-22-25-32(4)46(72-11)33(5)47-43(65)42(64)38(78-47)26-21-18-20-24-31(3)41(63)40-37(62)28-30-61(10)55(40)70/h15,17-28,30,33-36,38-39,42-53,56-57,63-68,71H,16,29H2,1-14H3,(H,60,69)/b17-15+,20-18+,23-22+,26-21+,27-19+,31-24+,32-25+,41-40+ | |
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Yes |
General status |
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Antibiotic, Antibacterial, Growth promoter | |
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Unclassified substance | |
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Natural | |
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Inhibits bacterial protein synthesis | |
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[50S ribosomal protein L10, Antagonist] | |
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56592-32-6 | |
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None allocated | |
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No | |
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1145.33 | |
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2-[2,3-dihydroxy-4-[3-hydroxy-5-(4-hydroxy-3,5-dimethoxy-6-methyloxan-2-yl)oxy-4-methoxy-6-methyloxan-2-yl]oxy-5,5-dimethyl-6-[(1E,3E)-penta-1,3-dienyl]oxan-2-yl]-N-[(2E,4E)-7-[3,4-dihydroxy-5-[(1E,3E,5E)-7-(2-hydroxy-1-methyl-4-oxopyridin-3-yl)-6-methyl-7-oxohepta-1,3,5-trienyl]oxolan-2-yl]-6-methoxy-5-methylocta-2,4-dienyl]butanamide | |
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31-O-[6-deoxy-4-O-(6-deoxy-2,4-di-O-methyl-a-L-mannopyranosyl)-3-O-methyl-b-D-allopyranosyl]-1-methylmocimycin | |
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Evidence of use in third world countries | |
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Pale yellow solid |
Commercial |
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Largely obsolete but may be available in some countries | |||
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Late 1970s, first synthesised; Early 1980s, introduced into vet medicine; Late 1990s, start of phase-out | |||
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It was exclusively marketed as a feed additive | |||
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Efrotomycin is produced through a microbial fermentation process using Nocardia lactamdurans, a soil-dwelling actinomycete. The organism is cultivated in a chemically defined or complex medium, often containing sources like monosodium glutamate and glycerol, which enhance yield when paired with sulphuric acid pH control. The fermentation is typically carried out in shaker flasks or fermentors, where temperature, nutrient feed rate, and sterilisation conditions are tightly regulated to optimise biosynthesis. Efrotomycin is a secondary metabolite, so its production peaks during the stationary phase of microbial growth. After fermentation, the compound is extracted, commonly using solvents like methanol or acetone-water-ammonia mixtures, and purified through filtration and chromatography. | |||
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As microbial-based products tend to use fermentation-based production processes rather than chemical synthesis, they typically have a lower fossil fuel input in formulation and active ingredient creation, and also have reduced downstream emissions due to biodegradability and minimal soil disruption, their life-cycle GHG emissions are expected to be low. Whilst hard and precise data is not available, broad estimates suggest that typically emissions are likely to be below 5 kg CO₂e/kg. |
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1000 | 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 |
Moderate | ||||||||
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Neutral media: 232nm, 327nm | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Environmental exposure possible via the faeces and urine of treated livestock |
Degradation |
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11.5 | R3 R = Peer reviewed scientific publications 5% faeces in soil mix 20°C3 = Unverified data of known source |
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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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92.8 | 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 ) 4 = Verified data |
Non-mobile | |||||||
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0.93 | ||||||||||
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USEPA data Kf range 8.34-294 mL g⁻¹, Kfoc range 575.5-11017 mL g⁻¹, 1/n range 0.787-1.05, Soils=4 | ||||||||||
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Fate indices |
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Known soil and groundwater metabolites |
None
Other known metabolites |
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efrotomycin B | - | Pig (Stomach) | - |
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Terrestrial ecotoxicology |
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> 7500 | 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 |
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> 1000 | 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 ) 4 = Verified data |
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Aquatic ecotoxicology |
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> 100 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Salmo gairdneri5 = Verified data used for regulatory purposes |
Low | ||||||||
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180 | 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 | ||||||||
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31 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Daphnia magna5 = Verified data used for regulatory purposes |
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General |
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High (class III) | - | - | ||||||||
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> 7500 | 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 |
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Subcutaneous LD₅₀ > 2000 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Mouse3 = Unverified data of known source |
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Largely metabolised and excreted via urine | R3 R = Peer reviewed scientific publications 3 = Unverified data of known source |
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Health issues |
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May cause diarrhoea |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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efrotomycin | ||
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efrotomycine | ||
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efrotomicina | ||
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Record last updated: | 08/09/2025 |
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 |