Diclazuril |
![]() Last updated: 07/09/2025 |
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(Also known as: dyclazuril) |
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A systemic, triazinone antiprotozoal and anticoccidial veterinary drug | |
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Used both as a treatment and as a preventative for infections caused by Isospora spp., Toxoplasma gondii, and Eimeria spp.It has also been used for treating coccidiosis. | |
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Sheep; Poultry; Rabbits; Horses; Cattle |
Approval status |
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Approved - usually available as a prescription only medicine to be authorised by suitably qualified person (POM-VPS) | |
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Approved |
Chemical structure |
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None | |
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C₁₇H₉Cl₃N₄O₂ | |
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C1=CC(=CC=C1C(C#N)C2=C(C=C(C=C2Cl)N3C(=O)NC(=O)C=N3)Cl)Cl | |
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No data | |
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ZSZFUDFOPOMEET-UHFFFAOYSA-N | |
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InChI=1S/C17H9Cl3N4O2/c18-10-3-1-9(2-4-10)12(7-21)16-13(19)5-11(6-14(16)20)24-17(26)23-15(25)8-22-24/h1-6,8,12H,(H,23,25,26) | |
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Yes |
General status |
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Coccidiostat, Antiparasitic, Antiprotozoal agent, Feed additive | |
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Benzeneacetonitrile derivative | |
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Synthetic | |
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Unclear but blocks the excretion of oocysts inducing an interruption of the life cycle of the parasites | |
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[Tubulin, Inhibition] | |
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101831-37-2 | |
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Antiparasitic products, insecticides & repellents: Antiprotozoals | |
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QP51AJ03 | |
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No | |
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Allowed substance (Table 1: Ruminants, Porcine) | |
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407.64 | |
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2-(4-chlorophenyl)-2-[2,6-dichloro-4-(3,5-dioxo-1,2,4-triazin-2-yl)phenyl]acetonitrile | |
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2,6-dichloro-a-(4-chlorophenyl)-4-(4,5-dihydro-3,5-dioxo-1,2,4-triazin-2(3H)-yl)benzeneacetonitrile | |
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Commercial |
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Current | |||||||||
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circa 1995, introduced | |||||||||
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Cocci-Drench Oral Suspension | MSD Animal Health UK Ltd | UK National authorisation | Prescription only medicine to be authorised by suitably qualified person (POM-VPS) | ||||||
Coxicert Oral Suspension | Chanelle Pharmaceuticals Manufacturing Ltd | GB National authorisation | Prescription only medicine to be authorised by suitably qualified person (POM-VPS) | |||||||
Vecoxan Oral Suspension | MSD Animal Health UK Ltd | UK National authorisation | Prescription only medicine to be authorised by suitably qualified person (POM-VPS) | |||||||
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Supplied as oral solutions and drenches | |||||||||
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The production of diclazuril involves a multi-step synthetic process starting from aromatic precursors such as 2,6-dichloro-4-nitroaniline or 3,4,5-trichloronitrobenzene. These compounds undergo diazotization and substitution reactions to form a key intermediate, which is then reduced and further modified through coupling with chlorohexylaminomethyl acetic acid. This intermediate is cyclised under reflux conditions using hexanoic acid and its anhydride, followed by hydrolysis and high-temperature desulfurisation to yield the final diclazuril compound. The synthesis typically includes column chromatography steps, which pose challenges for industrial scalability due to cost and safety concerns. As a result, efforts have been made to simplify the process and improve yield for commercial production. | |||||||||
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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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0.01 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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295 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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3.47 X 1004 | Calculated | - | |||||||
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4.54 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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5.92 | R4 R = Peer reviewed scientific publications 4 = Verified data |
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0.078 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Low volatility | ||||||||
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Degradation |
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205 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Persistent | |||||||
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Literature states DT₅₀: 303 days in sandy loam, 183 days loam and 130 days on silt loam. | ||||||||||
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Stable | R4 R = Peer reviewed scientific publications 4 = Verified data |
Stable | |||||||
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Stable in pH 5 to 9 but rapidly hydrolyzed above pH 9 | ||||||||||
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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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1012 | 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 |
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Literature values give Kd 204-1824 mL g⁻¹ | ||||||||||
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Fate indices |
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Known soil and groundwater metabolites |
None
Other known metabolites |
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4-amino-2,6-dichloro-alpha–(4-chlorophenyl) | - | Animal | - |
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Terrestrial ecotoxicology |
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> 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 |
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> 2150 | R4 R = Peer reviewed scientific publications Anas platyrhynchos4 = Verified data |
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> 1100 | R3 R = Peer reviewed scientific publications Lumbricus terrestris NOEL3 = Unverified data of known source |
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Aquatic ecotoxicology |
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0.58 | R4 R = Peer reviewed scientific publications Lepomis macrochirus4 = Verified data |
Moderate | ||||||||
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> 0.63 | R3 R = Peer reviewed scientific publications Daphnia magna3 = Unverified data of known source |
Moderate | ||||||||
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0.16 | R4 R = Peer reviewed scientific publications Daphnia magna4 = Verified data |
Moderate | ||||||||
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7.3 | R4 R = Peer reviewed scientific publications Chironomus tentans4 = Verified data |
Moderate | ||||||||
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> 1.0 | 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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> 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 | ||||||||
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2.24 | 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 |
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Majority (>80%) is eliminated, as the unchanged parent, via the faeces and the remainder in the urine | 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 ) 5 = Verified data used for regulatory purposes |
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Health issues |
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Possible liver toxicant |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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diclazuril | ||
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diclazurilo | ||
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Record last updated: | 07/09/2025 |
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 |