Tilmicosin |
![]() Last updated: 15/09/2025 |
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(Also known as: 20-deoxy-20-(3,5-dimethylpiperidin-1-yl)-desmycosin ; AH0230 / AH0470; tilmicosina) |
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A semi-synthetic macrolide antibiotic | |
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Used for the treatment and prevention of pneumonia associated with Pasteurella haemolytica, P. multocida, Actinobacillus pleuropneumoniae, mycoplasma species and other microorganisms | |
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Cattle; Sheep; Pigs; Poultry; Rabbits; Fish |
Approval status |
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Approved - usually approved as a prescription only medicine to be authorised by a veterinarian (POM-V) | |
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Approved |
Chemical structure |
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Tilmicosin exhibits geometrical isomerism, specifically cis-trans isomerism, due to the configuration around its double bonds and bulky substituents. The compound exists as a mixture of cis and trans isomers, with the cis-isomer being the predominant and pharmacologically active form. Typically, the technical material contains approximately 82–88% cis-isomers and 12–18% trans-isomers. | |
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C₄₆H₈₀N₂O₁₃ | |
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CCC1C(C=C(C=CC(=O)C(CC(C(C(C(CC(=O)O1)O)C)OC2C(C(C(C(O2)C)O)N(C)C)O)CCN3CC(CC(C3)C)C)C)C)COC4C(C(C(C(O4)C)O)OC)OC | |
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CC[C@@H]1[C@H](/C=C(/C=C/C(=O)[C@@H](C[C@@H]([C@@H]([C@H](C(CC(=O)O1)O)C)O[C@H]2[C@@H]([C@H]([C@@H]([C@H](O2)C)O)N(C)C)O)CCN3CC(CC(C3)C)C)C)\C)CO[C@H]4[C@@H]([C@@H]([C@@H]([C@H](O4)C)O)OC)OC | |
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JTSDBFGMPLKDCD-SWSPHLSKSA-N | |
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InChI=1S/C46H80N2O13/c1-13-36-33(24-57-46-44(56-12)43(55-11)40(53)31(8)59-46)19-25(2)14-15-34(49)28(5)20-32(16-17-48-22-26(3)18-27(4)23-48)42(29(6)35(50)21-37(51)60-36)61-45-41(54)38(47(9)10)39(52)30(7)58-45/h14-15,19,26-33,35-36,38-46,50,52-54H,13,16-18,20-24H2,1-12H3/b15-14+,25-19+/t26-,27+,28-,29+,30-,31-,32+,33-,35-,36-,38+,39-,40-,41-,42-,43-,44-,45+,46-/m1/s1 | |
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Yes |
General status |
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Antibiotic, Antibacterial, Antimicrobial, Medicinal drug, Medicated feed additive | |
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Macrolide | |
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Semi-synthetic | |
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Interferes with protein synthesis | |
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[50S rRNA, Antagonist] | |
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108050-54-0 | |
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5282521 | |
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Antiinfectants for systemic use: Antibacterials for systemic use | |
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QJ01FA91 | |
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No | |
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Allowed substance (Table 1: All food producing species) | |
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869.15 | |
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(4R,5S,6S,7R,9R,11E,13E,15R,16R)-6-[(2R,3R,4S,5S,6R)-4-(dimethylamino)-3,5-dihydroxy-6-methyloxan-2-yl]oxy-7-[2-[(3R,5S)-3,5-dimethylpiperidin-1-yl]ethyl]-16-ethyl-4-hydroxy-15-[[(2R,3R,4R,5R,6R)-5-hydroxy-3,4-dimethoxy-6-methyloxan-2-yl]oxymethyl]-5,9,13-trimethyl-1-oxacyclohexadeca-11,13-diene-2,10-dione | |
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4A-O-de(2,6-dideoxy-3-C-methyl-α-L-ribo-hexopyranosyl)-20-deoxy-20-(3,5-dimethyl-1-piperidinyl)-(20(cis: trans)) tylosin | |
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Commercial |
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Current | |||
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Late 1980s, first synthesised; 1990s, introduced commercially | |||
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A wide variety of formulations are available including solutions for injection, granules and premixed medicated feeds | |||
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The production of tilmicosin begins with tylosin fermentation broth, which serves as the primary raw material. This broth is first pretreated and filtered to isolate tylosin, which then undergoes a series of chemical transformations including extraction, ammoniation, hydrolysis, and acidification to convert it into tilmicosin base. A key step involves reacting tylosin with 3,5-dimethylpiperidine, forming the tilmicosin molecule through structural modification of the macrolide ring. The crude tilmicosin is then purified and dried, and optionally converted into tilmicosin phosphate via phosphorylation and spray drying for improved solubility and stability | |||
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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. However, the semi-synthetic nature of the production process for this substance is likely to increase emissions. |
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566000 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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107 | 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 |
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1.23 X 1005 | Calculated | - | |||||||
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5.09 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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13.16 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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UV max: 283nm = 22643 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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Substance may enter the environment via the faeces of treated animals or by leaching from spilt medicated feed. |
Degradation |
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64 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Moderately persistent | |||||||
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730 | 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 |
Very persistent | ||||||||
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USEPA data: suggests soil DT₅₀ >2 years; Literature variable & sparse (i) 45.9% decline in loam soil after 1 year, no decline in clay loam after 1 year (E3); (ii) >64 days (R3) | ||||||||||
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0.82 | E4 E = Manufacturers safety data sheets 4 = Verified data |
Fast | |||||||
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Not pH sensitive | ||||||||||
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Stable | E4 E = Manufacturers safety data sheets 4 = Verified data |
Stable | |||||||
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Stable at pH 5 & 7, DT₅₀ 156 days at pH 9 | ||||||||||
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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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178.5 | 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 ) 3 = Unverified data of known source |
Non-mobile | |||||||
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16319 | ||||||||||
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USEPA data: Kd range 86-318 mL g⁻¹, Koc range 4244-36150 mL g⁻¹, Soils=4 | ||||||||||
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Fate indices |
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-0.61 | Calculated | Low leachability | ||||||||||||||||||||||||||
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450 | V1 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Estimated1 = Estimated data with little or no verification |
Threshold for concern | |||||||||||||||||||||||||
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Not available | - |
Known soil and groundwater metabolites |
None
Other known metabolites |
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tilmicosin sulphate | - | Rat | - | ||||
N-desmethyl tilmicosin | - | Animal | - |
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Terrestrial ecotoxicology |
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> 800 | 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 ) Rat5 = Verified data used for regulatory purposes |
Moderate | ||||||||
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> 4710 mg kg feed⁻¹ | E4 E = Manufacturers safety data sheets Anas platyrhynchos4 = Verified data |
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> 918 | E3 E = Manufacturers safety data sheets Eisenia foetida 28 day3 = Unverified data of known source |
Moderate | ||||||||
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Aquatic ecotoxicology |
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851 | E4 E = Manufacturers safety data sheets Oncorhynchus mykiss4 = Verified data |
Low | ||||||||
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57.3 | E4 E = Manufacturers safety data sheets Daphnia magna4 = Verified data |
Moderate | ||||||||
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0.35 | E4 E = Manufacturers safety data sheets Raphidocelis subcapitata4 = Verified data |
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General |
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High (class III) | - | - | ||||||||
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> 800 | 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 ) Rat5 = Verified data used for regulatory purposes |
Moderate | ||||||||
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Very little metabolism, excreted unchanged predominately in the faeces | 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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Health issues |
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Severe allergen Cardiovascular toxicant |
Handling issues |
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May emit toxic fumes when heated to decomposition | |||
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Not listed (Not listed) | |||
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tilmicosin | ||
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tilmicosine | ||
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tilmicosina | ||
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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 |