Medetomidine |
![]() Last updated: 15/09/2025 |
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(Not known by any other names) |
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Medetomidine is a veterinary sedative analgesic often used in combination with opioids and used as the hydrochloride salt. | |
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Used as both a surgical anesthetic and an analgesic | |
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Deer; Cats; Dogs |
Approval status |
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Approved - usually available as a prescription-only-medicine to be authorised by a veterinarian (POM-V) | |
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Approved |
Chemical structure |
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Medetomidine exhibits optical isomerism, meaning it exists as two enantiomers: dexmedetomidine and levomedetomidine. These enantiomers differ in the spatial arrangement around a chiral centre, which significantly affects their biological activity. The dex- isomer is the pharmacologically active form, it binds selectively to alpha2-adrenergic receptors, producing sedation, analgesia, and anxiolysis. In contrast, levomedetomidine has minimal clinical effect and is generally considered inactive. Commercial medetomidine used in veterinary medicine is typically a racemic mixture, containing equal parts of both enantiomers. However, in human medicine, dexmedetomidine alone is preferred for its targeted action and reduced side effects. | |
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C₁₃H₁₆N₂ | |
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CC1=C(C(=CC=C1)C(C)C2=CN=CN2)C | |
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CUHVIMMYOGQXCV-UHFFFAOYSA-N | |
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InChI=1S/C13H16N2/c1-9-5-4-6-12(10(9)2)11(3)13-7-14-8-15-13/h4-8,11H,1-3H3,(H,14,15) | |
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Yes |
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Common Name | Relationship | Link |
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medetomidine hydrochloride | Variant | ![]() |
General status |
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Sedative, Analgesic | |
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Biocide; Antifouling agent | |
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Unclassified substance | |
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>99% | |
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Synthetic | |
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A non-narcotic alpha2-adrenoreceptor agonist | |
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[Alpha2-adrenergic, Agonist] | |
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86347-14-0 | |
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811-718-6 | |
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None allocated | |
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69602 | |
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No data found | |
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Nervous system: Psycholeptics | |
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QN05CM91 | |
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No | |
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200.28 | |
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(RS)-4-[1-(2,3-dimethylphenyl)ethyl]-3H-imidazole | |
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EU approval as antifouling agent until June 2026 | |
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White crystalline, odourless powder | |
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Commercial |
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Current | |||
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1990s, developed & registered | |||
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Usually formulated as injectable solutions | |||
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Medetomidine is synthesised through a multi-step organic process that typically begins with the preparation of a substituted imidazole derivative. One efficient route involves a nucleophilic addition reaction between 1-trityl imidazole-4-formaldehyde and 2,3-dimethylphenylmagnesium bromide to form a key intermediate. This is followed by a Wittig olefination step to introduce an alkenyl group, which is then subjected to hydrogenation to yield racemic medetomidine. The final product may be purified and resolved into its enantiomers, most notably dexmedetomidine, using chiral separation techniques such as crystallisation with (+)-tartaric acid. | |||
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Published GHG data is not available for most pharmaceuticals. However, according to industry, global averages suggest producing 1 kg of a typical active pharmaceutical ingredient can range from 10 to 100 kg CO₂e for small molecule drugs and potentially up to 1000 kg CO₂e for complex biologicals such as vaccines, depending on the drug type, its formulation, complexity of synthesis, solvent recovery, and energy sources used. |
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19800 | E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
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3300 | E3 E = Manufacturers safety data sheets p-Xylene3 = Unverified data of known source |
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65000 | E3 E = Manufacturers safety data sheets Acetone3 = Unverified data of known source |
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116 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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382 | E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
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191.3 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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7.94 X 1002 | Calculated | - | |||||||
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2.9 | E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
Moderate | ||||||||
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3.5 X 10-03 | E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
Low volatility | ||||||||
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Degradation |
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100 | E2 E = Manufacturers safety data sheets 2 = Unverified data of unknown source |
Persistent | |||||||
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Literature: Slow degradation | ||||||||||
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110 | E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
Slow | ||||||||
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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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Slightly mobile | |||||||
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2460 | ||||||||||
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Literature data range Koc 1215 to 3705 g/mL | ||||||||||
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Fate indices |
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1.22 | Calculated | Low leachability | ||||||||||||||||||||||||||
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Known metabolites |
None
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Terrestrial ecotoxicology |
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> 31.25 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
High | ||||||||
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Aquatic ecotoxicology |
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30.0 | E3 E = Manufacturers safety data sheets Danio rerio3 = Unverified data of known source |
Moderate | ||||||||
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4.5 | E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
Moderate | ||||||||
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0.005 | E3 E = Manufacturers safety data sheets Americamysis bahia as 28 day NOEC3 = Unverified data of known source |
High | ||||||||
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0.34 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Desmodesmus subspicatus3 = Unverified data of known source |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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> 31.25 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
High | ||||||||
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2000 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
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0.14 | E3 E = Manufacturers safety data sheets Rat 4 hr3 = Unverified data of known source |
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Metabolised and excreted via the kidneys in the urine. | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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Possible lungs, liver and kidney toxicant May cause hypersensitivity reactions Harmful if swallowed Has a strong sedative effect |
Handling issues |
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Emits a variety of toxic fumes on combustion Corrosive Not explosive or oxidising |
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Health: H300, H310 Environment: H400, H410 |
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Not listed (Not listed) | |||
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Not regulated | |||
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medetomidine | ||
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medetomidina | ||
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Record last updated: | 15/09/2025 |
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 |