| Tulathromycin A |
![]() Last updated: 16/09/2025 |
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(Not known by any other names) |
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A semi-synthetic macrolide veterinary drug | |
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Used to treat bovine and porcine respiratory diseases, infectious bovine keratoconjunctivitis and interdigital necrobacillosis | |
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Cattle; Pigs; Sheep |
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Approved - usually available as a prescription only medicine to be authorised by a veterinarian (POM-V) | |
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Approved |
| Chemical structure |
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Tulathromycin A exhibits stereoisomerism, specifically chirality, due to its complex macrolide structure containing multiple asymmetric carbon atoms. These chiral centres give rise to optical isomers. The biologically active form of tulathromycin A is defined by a precise configuration at each chiral centre. Tulathromycin exists as a mixture of isomers, primarily tulathromycin A and tulathromycin B, typically in a 9:1 ratio, with tulathromycin A being the dominant and therapeutically active component. | |
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C₄₁H₇₉N₃O₁₂ | |
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CCCNCC1(C(OC(CC1(C)OC)OC2C(C(C(CC(CNC(C(C(C(OC(=O)C2C)CC)(C)O)O)C)C)(C)O)OC3C(C(CC(O3)C)N(C)C)O)C)C)O | |
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CCCNC[C@@]1([C@@H](O[C@H](C[C@@]1(C)OC)O[C@H]2[C@@H]([C@H]([C@](C[C@H](CN[C@@H]([C@H]([C@]([C@H](OC(=O)[C@@H]2C)CC)(C)O)O)C)C)(C)O)O[C@H]3[C@@H]([C@H](C[C@H](O3)C)N(C)C)O)C)C)O | |
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GUARTUJKFNAVIK-KMKQSXFFSA-N | |
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InChI=1S/C41H79N3O12/c1-15-17-42-22-41(50)28(8)53-31(20-39(41,10)51-14)55-33-25(5)35(56-37-32(45)29(44(12)13)18-24(4)52-37)38(9,48)19-23(3)21-43-27(7)34(46)40(11,49)30(16-2)54-36(47)26(33)6/h23-35,37,42-43,45-46,48-50H,15-22H2,1-14H3/t23-,24-,25+,26-,27-,28+,29+,30-,31+,32-,33+,34-,35-,37+,38-,39-,40-,41+/m1/s1 | |
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Yes |
| General status |
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Antibiotic, Antibacterial, Medicinal drug | ||||||||||||||
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Macrolide | ||||||||||||||
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>940 g/Kg | ||||||||||||||
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Semi-synthetic | ||||||||||||||
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Inhibits protein synthesis by selectively binding to 23S ribosomal RNA | ||||||||||||||
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[23S rRNA, Antagonist] | ||||||||||||||
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217500-96-4 | ||||||||||||||
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9832301 | ||||||||||||||
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Antiinfectives for systemic use: Antibacterials for systemic use | ||||||||||||||
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QJ01FA94 | ||||||||||||||
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No | ||||||||||||||
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Allowed susbtance (Table 1: Bovince, Porcine) | ||||||||||||||
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806.23 | ||||||||||||||
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(2R,3S,4R,5R,8R,10R,11R,12S,13S,14R)-11-[(2S,3R,4S,6R)-4-(dimethylamino)-3-hydroxy-6-methyloxan-2-yl]oxy-2-ethyl-3,4,10-trihydroxy-13-[(2R,4R,5S,6S)-5-hydroxy-4-methoxy-4,6-dimethyl-5-(propylaminomethyl)oxan-2-yl]oxy-3,5,8,10,12,14-hexamethyl-1-oxa-6-azacyclopentadecan-15-one | ||||||||||||||
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White to off-white coloured solid | ||||||||||||||
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| Commercial |
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Current | |||
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Early 2000s, developed; 2003, first EU approvals | |||
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Usually supplied as solution for injection | |||
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Tulathromycin A is a semi-synthetic macrolide antibiotic is derived from fermentation of Streptomyces fradiae, which produces tylosin, a natural precursor. This fermentation step is essential, laying the biochemical foundation for tulathromycin’s complex structure. Following fermentation, the tylosin-derived intermediate undergoes a series of chemical transformations, including oxidation, reduction, and a Passerini reaction, to introduce key functional groups like the cyclopropyl and amido moieties. These steps culminate in the formation of tulathromycin A, with high selectivity and minimal by-products, making it suitable for industrial-scale synthesis. | |||
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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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190 | 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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1.17 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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8.49 | 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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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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| Known metabolites |
None
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| Terrestrial ecotoxicology |
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> 2000 | 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 |
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| Aquatic ecotoxicology |
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> 20 | 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 ) Cyprinodon variegatus marine species3 = Unverified data of known source |
Moderate | ||||||||
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> 20 | 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 magna 1 hr3 = Unverified data of known source |
Moderate | ||||||||
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| General |
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> 2000 | 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 |
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> 2000 | E3 E = Manufacturers safety data sheets Rabbit3 = Unverified data of known source |
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0.05 | 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 ) Rat SF=1005 = Verified data used for regulatory purposes |
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Excreted with some metabolism but mainly as the unchanged drug in the faeces and urine | 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 ) 5 = Verified data used for regulatory purposes |
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| Health issues |
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Possible liver toxicant May cause diarrhoea and other gastrointestinal problems |
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No information available | |||
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Not listed (Not listed) | |||
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tulathromycin A | ||
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| 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 |
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