Neomycin (Ref: USAF CB-19) |
![]() Last updated: 06/09/2025 |
![]() |
(Also known as: fradiomycin; neomycine; nivemycin; mycifradin) |
|
![]() |
|
A broad spectrum antibiotic effective against a wide range of bacteria | |
---|---|---|
|
Used to treat bacterial gastrointestinal infections and mastitis | |
|
Cats; Dogs; Fish; Cattle; Pigs; Sheep; Horses |
Approval status |
|
Approved - usually available as a prescription only medicine to be authorised by a veterinarian (POM-V) | |
---|---|---|
|
Approved |
Chemical structure |
|
Neomycin exhibits structural and stereoisomerism, primarily due to its complex arrangement of aminoglycoside sugar units and multiple chiral centres. It is a mixture of several closely related compounds, neomycin A, B, and C, with neomycin B (also known as framycetin) being the most pharmacologically active. Neomycin C is a stereoisomer of neomycin B, differing in the spatial configuration of one or more chiral centres, which can subtly affect its biological activity. Additionally, synthetic studies have produced glycosidic site isomers of neomycin B, where the linkage positions between sugar units vary resulting in pseudo-tetrasaccharides with distinct binding affinities to nucleic acid structures like DNA and RNA triplexes. | |
---|---|---|
|
C₂₃H₄₆N₆O₁₃ | |
|
C1C(C(C(C(C1N)OC2C(C(C(C(O2)CN)O)O)N)OC3C(C(C(O3)CO)OC4C(C(C(C(O4)CN)O)O)N)O)O)N | |
|
C1[C@H]([C@@H]([C@H]([C@@H]([C@H]1N)O[C@@H]2[C@@H]([C@H]([C@@H]([C@H](O2)CN)O)O)N)O[C@H]3[C@@H]([C@@H]([C@H](O3)CO)O[C@@H]4[C@@H]([C@H]([C@@H]([C@@H](O4)CN)O)O)N)O)O)N | |
|
PGBHMTALBVVCIT-VCIWKGPPSA-N | |
|
InChI=1S/C23H46N6O13/c24-2-7-13(32)15(34)10(28)21(37-7)40-18-6(27)1-5(26)12(31)20(18)42-23-17(36)19(9(4-30)39-23)41-22-11(29)16(35)14(33)8(3-25)38-22/h5-23,30-36H,1-4,24-29H2/t5-,6+,7-,8+,9-,10-,11-,12+,13-,14-,15-,16-,17-,18-,19-,20-,21-,22-,23+/m1/s1 | |
|
Yes |
General status |
|
Medicinal drug, Antibiotic; Antibacterial | |
---|---|---|
|
Aminoglycoside | |
|
- | |
|
- | |
|
Natural | |
|
Inhibits bacteria by suppressing protein synthesis and growth. | |
|
[30S ribosomal protein S12, Antagonist], [16S rRNA, Antagonist] | |
|
1404-04-2 | |
|
215-773-1 | |
|
- | |
|
006303 | |
|
- | |
|
Alimentary tract & metabolism: Intestinal anti-infectants | |
|
QA07AA51 | |
|
No | |
|
Allowed substance (Table 1: All food producing species) | |
|
614.64 | |
|
- | |
|
(1R,2R,3S,4R,6S)-4,6-diamino-2-{[3-O-(2,6-diamino-2,6-dideoxy-ß-L-idopyranosyl)- ß-D-ribofuranosyl]oxy}-3-hydroxycyclohexyl 2,6-diamino-2,6-dideoxy-a-D-glucopyranoside | |
|
- | |
|
- | |
|
- | |
|
- | |
|
Pale yellow to white coloured solid | |
|
Commercial |
|
|
|||
---|---|---|---|---|
|
Current | |||
|
1949, discovered;1952, first medical approval | |||
|
|
|||
|
|
|||
|
Available in a range of formulations including oral solutions, powders to add to drinking water and solutions for intramammary injections | |||
|
The production of neomycin begins with the fermentation of Streptomyces fradiae under carefully controlled conditions in large bioreactors. The fermentation medium typically contains carbohydrates (like glucose), nitrogen sources, vitamins, and minerals to optimise bacterial growth and antibiotic yield. Once fermentation is complete, the culture broth undergoes filtration to remove biomass, followed by extraction and purification steps to isolate neomycin. | |||
|
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. |
|
![]() |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
250 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Moderate | ||||||||
|
0.225 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Methanol3 = Unverified data of known source |
- | ||||||||
0.095 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Ethanol3 = Unverified data of known source |
- | |||||||||
0.05 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Benzene3 = Unverified data of known source |
- | |||||||||
0.08 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Cyclohexane3 = Unverified data of known source |
- | |||||||||
|
255 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
255 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
|
2.00 X 10-04 | Calculated | - | |||||||
|
-3.7 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Low | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
12.9 | R4 R = Peer reviewed scientific publications 4 = Verified data |
- | ||||||||
- | |||||||||||
|
- | - | - | ||||||||
|
4.1 X 10-08 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Non-volatile | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
1.541 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
- | ||||||||
|
- |
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 |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
> 200 | 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 |
Moderate | ||||||||
|
|
- | - | - | |||||||
|
- | - | |||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
- | |||||||||||
|
- | - | - | ||||||||
- | |||||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - |
Aquatic ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - |
|
- | - | - | |||
|
> 800 | 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 ) Crassostrea gigas Larva4 = Verified data |
- |
|
![]() |
General |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
High (class III) | - | - | ||||||||
|
> 200 | 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 |
Moderate | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
Intraperitoneal LD₅₀ = 116 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Mouse3 = Unverified data of known source |
- | ||||||||
Subcutaneous LD₅₀ = 633 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
- | |||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | |||||||||
|
- | ||||||||||
|
Up to 97% of oral dose excreted unchanged in faeces | R3 R = Peer reviewed scientific publications 3 = Unverified data of known source |
- |
Health issues |
|
|
||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
Kidney toxicant May cause dermatitis May impair hearing or cause vertigo |
Handling issues |
|
|
|||
---|---|---|---|---|
|
When heated to decomposition it emits acrid smoke & irritating fumes Hygroscopic |
|||
|
- | |||
|
Not listed (Not listed) | |||
|
- | |||
|
- | |||
|
- |
|
![]() |
|
|
||
---|---|---|---|
|
neomycin | ||
|
neomycine | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- |
Record last updated: | 06/09/2025 |
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 |