Gamithromycin |
![]() Last updated: 08/09/2025 |
![]() |
(Not known by any other names) |
|
![]() |
|
A macrolide veterinary drug active in vitro against certain bacterial agents | |
---|---|---|
|
Used to treat bovine respiratory disease associated with Mannheimia haemolytica, Pasteurella multocida and Histophilus somni | |
|
Cattle; Pigs; Sheep |
Approval status |
|
Approved | |
---|---|---|
|
Approved |
Chemical structure |
|
Gamithromycin exhibits stereoisomerism, specifically chirality, due to the presence of multiple asymmetric carbon atoms in its complex macrolide structure. As a 15-membered azalide ring antibiotic, it contains several chiral centres. These chiral centres give rise to optical isomers, but only one stereoisomer is biologically active and used therapeutically. | |
---|---|---|
|
C₄₀H₇₆N₂O₁₂ | |
|
CCCN1CC(C(C(C(OC(=O)C(C(C(C(C(CC1C)(C)O)OC2(C(C(CC(O2)C)N(C)C)O)C)C)OC3CC(C(C(O3)C)O)(C)OC)C)CC)(C)O)O)C | |
|
CCCN1C[C@@H]([C@H]([C@]([C@H](OC(=O)[C@@H]([C@H]([C@@H]([C@H]([C@](C[C@H]1C)(C)O)O[C@]2([C@@H]([C@H](C[C@H](O2)C)N(C)C)O)C)C)O[C@H]3C[C@]([C@@H]([C@H](O3)C)O)(C)OC)C)CC)(C)O)O)C | |
|
IMIKDFRXJJEHPP-KXHBJKOVSA-N | |
|
InChI=1S/C41H78N2O12/c1-16-18-43-22-23(3)33(44)40(11,49)30(17-2)52-37(47)27(7)32(53-31-21-39(10,50-15)34(45)28(8)51-31)26(6)36(38(9,48)20-24(43)4)55-41(12)35(46)29(42(13)14)19-25(5)54-41/h23-36,44-46,48-49H,16-22H2,1-15H3/t23-,24+,25+,26-,27+,28+,29-,30+,31-,32-,33+,34+,35+,36+,38+,39-,40+,41-/m0/s1 | |
|
Yes |
General status |
|
Antimicrobial, Antibiotic, Antibacterial, Medicinal drug | |
---|---|---|
|
Macrolide | |
|
- | |
|
- | |
|
Semi-synthetic | |
|
Broad-spectrum, distrupts bacterial protein synthesis | |
|
[50S rRNA, Antagonist] | |
|
145435-72-9 | |
|
- | |
|
- | |
|
- | |
|
- | |
|
Antiinfectives for systemic use: Antibacterials for systemic use | |
|
QJ01FA95 | |
|
No | |
|
Allowed substance (Table 1: Bovine) | |
|
777.04 | |
|
- | |
|
(2R,3S,5R,6R,8R,11S,12R,13S,14R)-5-[(2S,3R,4S,6R)-4-(dimethylamino)-3-hydroxy-6-methyloxan-2-yl]oxy-14-ethyl-6,12,13-trihydroxy-3-[(2R,4R,5S,6S)-5-hydroxy-4-methoxy-4,6-dimethyloxan-2-yl]oxy-2,4,6,8,11,13-hexamethyl-9-propyl-15-oxa-9-azacyclopentadecan-1-one | |
|
3,5,8,10,12,14-hexamethyl-7-propyl-11-[[3,4,6-trideoxy-3-(dimethylamino)-b-D-xylo-hexopyranosyl]oxy]-1-oxa-7-azacyclopentadecan-15-one | |
|
- | |
|
- | |
|
- | |
|
White to beige coloured crystalline powder |
Commercial |
|
|
|||
---|---|---|---|---|
|
Current | |||
|
2010s, introduced; 2017, high purity sysnthesis methods developed | |||
|
|
|||
|
|
|||
|
Usually supplied as a solution for injection | |||
|
The process begins with microbial fermentation, typically using Saccharopolyspora erythraea or related actinomycetes, to produce a macrolide precursor such as 9-deoxy-8a-aza-8a-homoerythromycin A. This compound is structurally related to erythromycin and serves as the foundation for gamithromycin. After fermentation, the precursor undergoes semi-synthetic chemical modifications, including reductive amination, deprotection, and crystallisation, to yield the final active molecule with high purity | |||
|
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. |
|
![]() |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
- | |||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- |
Degradation |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
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 |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
- | ||||||||||
|
- |
Fate indices |
|
|
|
|
||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||||||||||||||||||||
|
|
- | - | - | |||||||||||||||||||||||||
|
- | - |
Known metabolites |
None
|
![]() |
Terrestrial ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
> 2000 | 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 |
Low | ||||||||
|
|
- | - | - | |||||||
|
- | - | |||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
- | |||||||||||
|
- | - | - | ||||||||
- | |||||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - |
Aquatic ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - |
|
- | - | - | |||
|
- | - | - |
|
![]() |
General |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
High (class III) | - | - | ||||||||
|
> 2000 | 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 |
Low | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
0.01 | 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 |
- | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | |||||||||
|
- | ||||||||||
|
Eliminated primarily via the faeces (around 40-60%) and lesser amounts (<20%) in the 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 |
- |
Health issues |
|
|
||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
No further information available |
Handling issues |
|
|
|||
---|---|---|---|---|
|
No information available | |||
|
- | |||
|
Not listed (Not listed) | |||
|
- | |||
|
- | |||
|
- |
|
![]() |
|
|
||
---|---|---|---|
|
gamithromycin | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- |
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 |