Chlortetracycline |
![]() Last updated: 05/09/2025 |
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(Also known as: aureomycin ; biomycin ) |
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Broad spectrum antibiotic and antimicrobial substance isolated from the microorganism (treptomyces aureofaciens) used in veterinary products and for aquaculture. Usually formulated as the hydrochloride salt. | |
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Mainly used for the prevention of infections of superficial traumatic or surgical wounds | |
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Agricultural livestock including: Poultry, Pigs, Cattle and Fish |
Approval status |
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Approved - usually available as a veterinary medicine for general sale (AVM-GSL) | |
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Approved |
Chemical structure |
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Chlortetracycline exhibits complex isomerism due to its multiple chiral centres and tautomeric forms. The molecule contains several asymmetric carbon atoms that give rise to stereoisomers that differ in spatial arrangement but share the same molecular formula. Additionally, chlortetracycline undergoes tautomerism, especially in aqueous solutions and under varying pH conditions, where keto-enol shifts and epimerization at the C-4 position can occur, forming 4-epichlortetracycline and other isomeric species. | |
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C₂₂H₂₃ClN₂O₈ | |
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CC1(C2CC3C(C(=O)C(=C(C3(C(=O)C2=C(C4=C(C=CC(=C41)Cl)O)O)O)O)C(=O)N)N(C)C)O | |
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C[C@@]1([C@H]2C[C@H]3[C@@H](C(=O)C(=C([C@]3(C(=O)C2=C(C4=C(C=CC(=C41)Cl)O)O)O)O)C(=O)N)N(C)C)O | |
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DHPRQBPJLMKORJ-XRNKAMNCSA-N | |
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InChI=1S/C22H23ClN2O8/c1-21(32)7-6-8-15(25(2)3)17(28)13(20(24)31)19(30)22(8,33)18(29)11(7)16(27)12-10(26)5-4-9(23)14(12)21/h4-5,7-8,15,26-27,30,32-33H,6H2,1-3H3,(H2,24,31)/t7-,8-,15-,21-,22-/m0/s1 | |
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Yes |
General status |
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Bactericide, Fungicide, Antimicrobial, Medicated feed additive | |
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Wood preservative; Antimicrobial; Biocide | |
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Amide pesticide; Tetracycline compound | |
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Natural | |
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Protein synthesis inhibitor | |
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[16S ribosomal RNA, Inhibitor], [30S ribosomal proteins, Inhibitor], [ADP-ribosylation factor 1, Inhibitor], [Catalase, Inhibitor], [Ephrin type-B receptor 1, Inhibitor], [Pancreatic triacylglycerol lipase, Inhibitor], [Protein-arginine deiminase type-4, Inhibitor] | |
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57-62-5 | |
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200-341-7 | |
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006301 | |
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54675777 | |
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Dermatologicals: Antibiotics & chemotherapeutics for dermatological use | |
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QD06AA52 | |
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No | |
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Allowed substance (Table 1: All food producing species) | |
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478.88 | |
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(4S,4aS,5aS,6S,12aR)-7-chloro-4-(dimethylamino)-1,6,10,11,12a-pentahydroxy-6-methyl-3,12-dioxo-4,4a,5,5a-tetrahydrotetracene-2-carboxamide | |
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7-chlorotetracycline | |
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Possible groundwater contaminant | |
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White crystalline solid | |
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Commercial |
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Current | |||
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1945, first discovered | |||
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Usually supplied in formualtions for oral administration and medicated feed premixes | |||
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Chlortetracycline is produced through a fermentation process using the bacterium Streptomyces aureofaciens. The production begins with inoculum development, where spores are cultivated in a nutrient-rich medium containing carbohydrates like sucrose and maltose, nitrogen sources such as corn-steep liquor and peanut meal, and buffering agents like calcium carbonate. Once the culture is established, it undergoes submerged aerobic fermentation at controlled temperatures (28–30 DegC) and pH (6–6.5) for several days, during which chlortetracycline is biosynthesised. After fermentation, the broth is acidified and filtered to separate the mycelium. The antibiotic is then extracted from the filtrate using solvents like 2-ethoxyethanol and purified through precipitation and crystallisation steps. | |||
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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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630 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Moderate | ||||||||
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168.5 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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2.40 X 10-01 | Calculated | - | |||||||
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-0.62 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low | ||||||||
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4.5 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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2.09 X 10-23 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Low volatility | ||||||||
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4.8 X 10-22 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Non-volatile | ||||||||
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Substance may enter the environment via the faeces of treated animals or by leaching from spilt medicated feed. Identified in pig manure at high concentrations implying manure implying a major release route |
Degradation |
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30 | R3 R = Peer reviewed scientific publications 3 = Unverified data of known source |
Moderately persistent | |||||||
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General literature DT₅₀ range >30 days (R3) | ||||||||||
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44% lost after 30 days | R3 R = Peer reviewed scientific publications Soil and poultry manure at 30°C decreases with decreasing temp. DT₅₀ range 0.1-56 days3 = Unverified data of known source |
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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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Fate indices |
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Low risk | Q3 Q = Miscellaneous data from online sources Based on LogP < 33 = Unverified data of known source |
Low risk | |||||||||||||||||||||||||
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Known metabolites |
None
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Terrestrial ecotoxicology |
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> 1500 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Mouse3 = Unverified data of known source |
Moderate | ||||||||
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Aquatic ecotoxicology |
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> 0.89 | R4 R = Peer reviewed scientific publications Unknown species4 = Verified data |
Moderate | ||||||||
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128 | 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 magna3 = Unverified data of known source |
Low | ||||||||
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1.62 | 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 ) Lemna gibba3 = Unverified data of known source |
Moderate | ||||||||
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3.1 | R3 R = Peer reviewed scientific publications Raphidocelis subcapitata3 = Unverified data of known source |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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> 1500 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Mouse3 = Unverified data of known source |
Moderate | ||||||||
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Intraperitoneal LDLo = 335 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Intravenous LD₅₀ = 118 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Mainly eliminated in the faeces | R4 R = Peer reviewed scientific publications 4 = Verified data |
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Health issues |
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No further information available |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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chlortetracycline | ||
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chlortetracycline | ||
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clortetraciclina | ||
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Record last updated: | 05/09/2025 |
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 |