Oxytetracycline hydrochloride |
![]() Last updated: 16/09/2025 |
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(Also known as: terramycin; oxytracyl; oxytetrin; terramitsin; oxitetracycline; crop antibiotic) |
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A highly active broad spectrum antibiotic used to control infection animals diseses and bacterial pathogens | |
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Used to control gastrointestinal and respiratory diseases as well as some skin conditions including Rickettsial infections, Lupus | |
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Calves; Non-lactating dairy cattle; Beef; Pigs; Fish; Poultry; Cats; Dogs |
Approval status |
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Approved - usually supplied as a prescription only medicine to be authorised by a veterinarian (POM-V) | |
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Approved |
Chemical structure |
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Oxytetracycline hydrochloride exhibits stereoisomerism, particularly epimerism and tautomerism, due to its multiple chiral centres and functional groups capable of rearrangement. The molecule contains several asymmetric carbon atoms, notably at positions 4, 4a, 5, 5a, 6, and 12a, which allow for the formation of diastereomers. One common isomeric form is 4-epioxytetracycline, which arises from inversion at the C-4 position and can occur spontaneously in aqueous solutions, especially under acidic conditions. Additionally, oxytetracycline undergoes tautomerism involving its keto and enol groups, particularly in the diketone and hydroxyl regions of the tetracycline ring system. Only one stereoisomer is used therapeutically. | |
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C₂₂H₂₅ClN₂O₉ | |
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CC1(C2C(C3C(C(=O)C(=C(C3(C(=O)C2=C(C4=C1C=CC=C4O)O)O)O)C(=O)N)N(C)C)O)O.Cl | |
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C[C@@]1([C@H]2[C@@H]([C@H]3[C@@H](C(=O)C(=C([C@]3(C(=O)C2=C(C4=C1C=CC=C4O)O)O)O)C(=O)N)N(C)C)O)O.Cl | |
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SVDOODSCHVSYEK-IFLJXUKPSA-N | |
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Yes |
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Common Name | Relationship | Link |
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oxytratracycline | Parent | ![]() |
General status |
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Bactericide, Antimicrobial, Antiseptic, Medicated feed additive | |
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Antimicrobial; Bactericide; Crop antibiotic | |
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Micro-organism derived substance | |
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Natural | |
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Broad-spectrum, protein synthesis inhibitor and binds to the 30S and 50S bacterial ribosomal subunits | |
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[30S ribosomal protein S9, Antagonist], [30S ribosomal protein S4, Antagonist], [16S rRNA, Antagonist] | |
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2-58-46-0 | |
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218-161-2 | |
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Dermatologicals: Antibiotics and chemotherapeutics for dermatological use; Antiinfectants for systemic use: Antibacterials for systemic use | |
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QD06AA03 for topical use; QJ01AA06 for systemic use; Others available | |
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No | |
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Allowed substance (Table 1: All food producing species) | |
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496.90 | |
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(4S,4aR,5S,5aR,6S,12aR)-4-(dimethylamino)-1,5,6,10,11,12a-hexahydroxy-6-methyl-3,12-dioxo-4,4a,5,5a-tetrahydrotetracene-2-carboxamide;hydrochloride | |
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(4S,4aR,5S,5aR,6S,12aR)-4-(dimethylamino)-1,5,6,10,11,12a-hexahydroxy-6-methyl-3,12-dioxo-4,4a,5,5a-tetrahydrotetracene-2-carboxamide;hydrochloride | |
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Possible groundwater contaminant | |
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Yellow crystalline powder | |
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Commercial |
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Current | |||
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1945, discovered; 1949, marketing launch; 1950s, first vet approvals | |||
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Supplied as a water soluble powder for preparation as injection when used as a veterinary product. For crop protection it is used as a foliar spray | |||
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Oxytetracycline hydrochloride is produced through a multi-stage process that begins with fermentation using Streptomyces rimosus, a soil-dwelling bacterium known for its ability to biosynthesise tetracycline antibiotics. During fermentation, the organism converts simple carbon sources into oxytetracycline via a polyketide synthase pathway, forming a tetracyclic ring structure through sequential condensation and cyclisation reactions. After fermentation, the broth is filtered to isolate crude oxytetracycline, which is then purified through solvent extraction and crystallisation. To form the hydrochloride salt, hydrogen chloride is introduced, often in a solvent system like n-butanol and isopropanol, facilitating salt formation and recrystallisation into a stable dihydrate form. | |||
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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. |
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6900 | R4 R = Peer reviewed scientific publications 4 = Verified data |
High | ||||||||
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121 | L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
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6.03 X 10-02 | Calculated | - | |||||||
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-1.22 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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1.63 | Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
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4.5 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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Weak acid | |||||||||||
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1.29 X 10-19 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) at 25 °C3 = Unverified data of known source |
Low volatility | ||||||||
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1.72 X 10-20 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) at 25 °C3 = Unverified data of known source |
Non-volatile | ||||||||
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Substance may enter the environment via the urine of treated animals. Monitoring studies have identified this substance in livestock liquid manures |
Degradation |
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18 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Non-persistent | |||||||
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21 | 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-persistent | ||||||||
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Literature estimates give DT₅₀ 1 to 10 wks | ||||||||||
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43.8 | R4 R = Peer reviewed scientific publications Aerobic sediment slurry; Other data DT₅₀ (1) 79 days slurry; (2) 12,0-15.4 day slurry4 = Verified data |
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9 | R3 R = Peer reviewed scientific publications 3 = Unverified data of known source |
Moderately fast | ||||||||
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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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698 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Non-mobile | |||||||
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52875 | ||||||||||
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Literature data: Kd range 417-1626 mL g⁻¹, Koc range 27792-93317 mL g⁻¹, soils=4; Other Literature data 27792-93317 generally quoted for tetracyclines (R4) | ||||||||||
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Fate indices |
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-0.96 | Calculated | Low leachability | ||||||||||||||||||||||||||
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0.6 | J2 J = Pesticide Action Network database (click here ) Mollusca2 = Unverified data of unknown source |
Low potential | |||||||||||||||||||||||||
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Not available | - |
Known metabolites |
None
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Terrestrial ecotoxicology |
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> 4800 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Low | ||||||||
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> 5620 | 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 ) Anas platyrhynchos4 = Verified data |
Low | ||||||||
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1954 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Low | ||||||||
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100 | 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 |
Moderate | ||||||||
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Aquatic ecotoxicology |
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116 | 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 ) Oncorhynchus mykiss4 = Verified data |
Low | ||||||||
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102 | 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 ) Daphnia magna4 = Verified data |
Low | ||||||||
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46.2 | R3 R = Peer reviewed scientific publications Daphnia magna3 = Unverified data of known source |
Low | ||||||||
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0.342 | R4 R = Peer reviewed scientific publications Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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0.183 | R4 R = Peer reviewed scientific publications Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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> 4800 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Low | ||||||||
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5700 | L3 L = Pesticide manuals and hard copy reference books / other sources Mouse3 = Unverified data of known source |
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Intraperitoneal LD₅₀ = 260 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Mouse3 = Unverified data of known source |
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Intravenous LD₅₀ = 260 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Systemically available oxytetracycline was primarily excreted in the urine and bile | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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May cause hypersensitivity reactions May cause tooth discoloration |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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oxytetracycline hydrochloride | ||
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oxytetracycline | ||
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Oxytetracyclin | ||
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oxytetracyclin | ||
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oxytetracicline | ||
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oxitetraciclina | ||
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oksytetracyklina | ||
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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 |