Butaphosphan |
![]() Last updated: 16/09/2025 |
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(Also known as: butafosfan) |
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An organic source of phosphorus used in veterinary medicine | |
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Used mainly as a supportive treatment of metabolic or reproductive disorders as well as developmental and nutritional disorders | |
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Cattle; Horses; Pigs, Sheep and goats; Dogs; Cats |
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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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None | |
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C₇H₁₈NO₂P | |
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CCCCNC(C)(C)P(=O)O | |
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WCXWARPXYQCRPP-UHFFFAOYSA-N | |
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InChI=1S/C7H18NO2P/c1-4-5-6-8-7(2,3)11(9)10/h8,11H,4-6H2,1-3H3,(H,9,10) | |
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Yes |
General status |
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Mineral supplement | |
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Phosphonic acid derivative | |
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Synthetic | |
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Mineral supplementation and electrolyte replacement agent | |
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[Cellular resilience, Enhancement] | |
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17316-67-5 | |
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241-341-7 | |
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72084 | |
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Alimentary tract and metabolism; mineral supplements; other mineral products, combinations | |
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QA12CX99 | |
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No | |
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179.20 | |
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2-(butylamino)propan-2-ylphosphinic acid | |
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Commercial |
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Current | |||
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1990s, developed | |||
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Usually formulated, along with cyanocobalamin, as a solution for injection | |||
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The production of butaphosphan involves a multi-step synthesis that begins by reacting n-butylamine with acetone in the presence of a molecular sieve, under controlled heating and stirring to form an imine intermediate. Once cooled to around 20–25 DegC, hypophosphorous acid is added, initiating a condensation reaction that yields a crude butaphosphan product. This mixture is then subjected to centrifugation to separate solids, followed by ethanol extraction and activated carbon treatment to remove impurities. The solution is heated to approximately 70 DegC, then cooled to 10 DegC in a crystallisation vessel to precipitate the purified compound. Final steps include centrifugation and drying, resulting in high-purity butaphosphan. | |||
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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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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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Fate indices |
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Known metabolites |
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Terrestrial ecotoxicology |
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16000 | 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 ) Mouse5 = Verified data used for regulatory purposes |
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Aquatic ecotoxicology |
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General |
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High (class III) | - | - | ||||||||
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16000 | 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 ) Mouse5 = Verified data used for regulatory purposes |
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Subcutaneous LD₅₀ = 21000 mg kg⁻¹ | 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 ) Mouse5 = Verified data used for regulatory purposes |
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Intravenous LD₅₀ = 10000 mg kg⁻¹ | 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 ) Mouse5 = Verified data used for regulatory purposes |
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Elimination is rapid, Within 12 hrs of intravenous administration 70-90% are excreted in urine. Very little is lost via faeces. | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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Not highly toxic High doses may cause cyanosis, excitability, diarrhoea |
Handling issues |
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No information available | |||
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Health: H315, H319 | |||
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Not listed (Not listed) | |||
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butaphosphan | ||
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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 |