Kanamycin |
![]() Last updated: 08/09/2025 |
![]() |
(Also known as: Nebramycin Factor 5; aminodeoxykanamycin; KAN) |
|
![]() |
|
An antibacterial drug active against both gram-negative and to a lesser extent gram-positive bacteria | |
---|---|---|
|
Used, for example, to treat clinical mastitis in lactating dairy cows and other bacterial infections | |
|
Cattle; Horses; Pigs; Sheep; Goats; Poultry |
Approval status |
|
Approvedv- usually available as a prescription only medicine to be authorised by a veterinarian (POM-V) | |
---|---|---|
|
Approved |
Chemical structure |
|
Kanamycin exhibits constitutional isomerism, primarily through its naturally occurring variants: kanamycin A, B, C, and D. These isomers share the same molecular formula but differ in the arrangement of functional groups, particularly the positioning of amino and hydroxyl groups on the sugar moieties and the central cyclohexane ring. Kanamycin A is the most pharmacologically active and widely used form, while the others, B, C, and D, are minor components formed during fermentation by Streptomyces kanamyceticus. These structural differences influence their binding affinity to bacterial ribosomal RNA, which is the primary target of aminoglycoside antibiotics. Although they are not stereoisomers, their distinct connectivity patterns result in varied biological activity and toxicity profiles, making kanamycin A the preferred therapeutic agent. | |
---|---|---|
|
C₁₈H₃₆N₄O₁₁ | |
|
C1C(C(C(C(C1N)OC2C(C(C(C(O2)CN)O)O)O)O)OC3C(C(C(C(O3)CO)O)N)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)O)O)O[C@@H]3[C@@H]([C@H]([C@@H]([C@H](O3)CO)O)N)O)N | |
|
SBUJHOSQTJFQJX-NOAMYHISSA-N | |
|
InChI=1S/C18H36N4O11/c19-2-6-10(25)12(27)13(28)18(30-6)33-16-5(21)1-4(20)15(14(16)29)32-17-11(26)8(22)9(24)7(3-23)31-17/h4-18,23-29H,1-3,19-22H2/t4-,5+,6-,7-,8+,9-,10-,11-,12+,13-,14-,15+,16-,17-,18-/m1/s1 | |
|
Yes |
General status |
|
Antibiotic, Antibacterial, Medicinal drug | |
---|---|---|
|
Aminoglycoside | |
|
- | |
|
- | |
|
Natural | |
|
Inhibits protein synthesis | |
|
[16S rRNA, Antagonist], [30S ribosomal protein S12, Antagonist] | |
|
59-01-8 | |
|
200-411-7 | |
|
- | |
|
- | |
|
- | |
|
Antiinfectives for systemic use: Antibacterials for intramammary use | |
|
QJ51RD01 | |
|
No | |
|
Allowed substance [Table 1: all food producing species except fin fish] | |
|
484.50 | |
|
- | |
|
2-(aminomethyl)- 6-[4,6-diamino-3- [4-amino-3,5-dihydroxy-6-(hydroxymethyl) tetrahydropyran-2-yl]oxy- 2-hydroxy- cyclohexoxy]- tetrahydropyran- 3,4,5-triol | |
|
- | |
|
- | |
|
- | |
|
- | |
|
- | |
|
Commercial |
|
|
|
|
|
||||||
---|---|---|---|---|---|---|---|---|---|---|
|
Current | |||||||||
|
1957, discovered | |||||||||
|
Ubrolexin Intramammary Suspension for Lactating Dairy Cows | Boehringer Ingelheim Animal Health UK Ltd | GB National authorisation | Prescription only medicine to be authorised by a veterinarian (POM-V) | ||||||
|
Current available products are formulated as intramammary suspension solutions for injection | |||||||||
|
Kanamycin is produced through a microbial fermentation process using Streptomyces kanamyceticus, a soil-derived actinomycete that naturally synthesises the antibiotic. The production begins with strain selection and genetic optimization to ensure high-yield output, followed by cultivation in a nutrient-rich medium under controlled conditions of pH, temperature, and aeration. During fermentation, kanamycin is secreted as a secondary metabolite, typically over several days. Once fermentation is complete, the broth undergoes extraction and purification, often involving adsorption to activated carbon, cation-exchange resins, and acid methanol elution to isolate the active compound. The purified kanamycin is then crystallised and formulated into pharmaceutical-grade products. | |||||||||
|
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. |
|
![]() |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
1000000 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
High | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
2.00 X 10-07 | Calculated | - | |||||||
|
-6.7 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
7.2 | R4 R = Peer reviewed scientific publications 4 = Verified data |
- | ||||||||
- | |||||||||||
|
4.39 X 10-18 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low volatility | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- |
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 |
|
|
|
|
||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||||||||||||||||||||
|
|
Low risk | Q3 Q = Miscellaneous data from online sources Based on LogP < 33 = Unverified data of known source |
Low risk | |||||||||||||||||||||||||
|
- | - |
Known metabolites |
None
|
![]() |
Terrestrial ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
> 5000 | 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) | - | - | ||||||||
|
> 5000 | 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 | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
Subcutaneous LD₅₀ = 4070 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
- | ||||||||
Intraperitoneal LD₅₀ = 1515 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
- | |||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | |||||||||
|
- | ||||||||||
|
Mainly unmetabolised and excreted 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 |
- |
Health issues |
|
|
||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
May trigger allergic reactions May damage hearing Possible kidney toxicant May cause nephrotoxicity May cause gastrointestinal problems |
Handling issues |
|
|
|||
---|---|---|---|---|
|
No information available | |||
|
- | |||
|
Not listed (Not listed) | |||
|
- | |||
|
- | |||
|
- |
|
![]() |
|
|
||
---|---|---|---|
|
kanamycin | ||
|
kanamycine | ||
|
- | ||
|
- | ||
|
kanamicina | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- |
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 |