Lubabegron fumerate (Ref: LY-488756) |
![]() Last updated: 15/09/2025 |
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(Also known as: lubabegron) |
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A veterinary drug consisting of freebase lubabegron and fumaric acid in the ratio 2:1. | |
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Used to reduce ammonia emissions from animals and their waste | |
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Cattle |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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Lubabegron fumarate exhibits stereoisomerism due to the presence of a single chiral centre in its molecular structure, which is located on the beta-carbon of the hydroxypropyl side chain, which is attached to the amine group. The biologically active form is the (2S)-enantiomer. The fumarate component is a geometric (E/Z) isomer, with the fumaric acid existing in the trans (E) configuration, which contributes to the salt’s stability and solubility but does not affect chirality. | |
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C₆₂H₆₂N₆O₁₀S₂ | |
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CC(C)(CC1=CC=C(C=C1)OC2=C(C=CC=N2)C#N)NCC(COC3=CC=CC=C3C4=CC=CS4)O.CC(C)(CC1=CC=C(C=C1)OC2=C(C=CC=N2)C#N)NCC(COC3=CC=CC=C3C4=CC=CS4)O.C(=CC(=O)O)C(=O)O | |
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CC(C)(CC1=CC=C(C=C1)OC2=C(C=CC=N2)C#N)NC[C@@H](COC3=CC=CC=C3C4=CC=CS4)O.CC(C)(CC1=CC=C(C=C1)OC2=C(C=CC=N2)C#N)NC[C@@H](COC3=CC=CC=C3C4=CC=CS4)O.C(=C/C(=O)O)\C(=O)O | |
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MEEKSPBNXICJNQ-CXUXXADZSA-N | |
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InChI=1S/2C29H29N3O3S.C4H4O4/c2*1-29(2,17-21-11-13-24(14-12-21)35-28-22(18-30)7-5-15-31-28)32-19-23(33)20-34-26-9-4-3-8-25(26)27-10-6-16-36-27;5-3(6)1-2-4(7)8/h2*3-16,23,32-33H,17,19-20H2,1-2H3;1-2H,(H,5,6)(H,7,8)/b;;2-1+/t2*23-;/m00./s1 | |
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Yes |
General status |
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Ammonia suppressant | |
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Unclassified substance | |
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Synthetic | |
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Lubabegron has three main mechanisms (1) improved responsiveness to insulin, (2) reduced blood urea nitrogen, and (3) increased use of amino acids for muscle protein synthesis | |
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[Beta3-Adrenergic receptor, Agonist], [Beta1 & Beta2-Adrenergic receptor, Antagonist] | |
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391926-19-5 | |
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691-417-2 | |
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71587727 | |
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Miscellaneous non-therapeutic agents | |
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QV07AQ01 | |
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No | |
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1115.3 | |
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(E)-but-2-enedioic acid;2-[4-[2-[[(2S)-2-hydroxy-3-(2-thiophen-2-ylphenoxy)propyl]amino]-2-methylpropyl]phenoxy]pyridine-3-carbonitrile | |
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Commercial |
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Current | |||
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2018, first registration USA | |||
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Usually formulated as a Type A Medicated Article, intended to be mixed into cattle feed. | |||
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The production of lubabegron fumarate begins with the multi-step chemical synthesis of its core structure, a substituted pyridine-carbonitrile scaffold. The process involves stereoselective alkylation to introduce the (2S)-hydroxypropylamine side chain, followed by etherification with a thiophenyl-phenoxy moiety to form the full pharmacophore. Once the active base compound is synthesised and purified, typically via chromatographic separation, it is reacted with fumaric acid to form the fumarate salt. | |||
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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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6.01 | 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 ) 4 = Verified data |
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175.4 | 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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3.98 X 1003 | Calculated | - | |||||||
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3.60 | 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 ) 4 = Verified data |
High | ||||||||
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5.46 | 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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PKa(2)=8.86 | |||||||||||
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10100 | F2 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 ) 2 = Unverified data of unknown source |
Highly volatile. If applied directly to plants or soil, drift is a concern & mitigation is advisable | ||||||||
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The primary route of environmental exposure to lubabegron will be from cattle manure spread to land |
Degradation |
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513 | 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 ) 4 = Verified data |
Very persistent | |||||||
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513 | 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 ) 4 = Verified data |
Very persistent | ||||||||
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1706 | 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 ) 4 = Verified data |
Very persistent | ||||||||
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USEPA data: Lab studies DT₅₀ range 289-866 days, Dt90 range 960-2879 days, Soils=4 | ||||||||||
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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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3557 | 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 ) 4 = Verified data |
Non-mobile | |||||||
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198988 | ||||||||||
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USEPA data: Kd range 3051-3887 mL g⁻¹, Koc range 47347-370420 mL g⁻¹, Soils=5 | ||||||||||
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Fate indices |
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-3.52 | Calculated | Low leachability | ||||||||||||||||||||||||||
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Known metabolites |
None
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Terrestrial ecotoxicology |
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1000 | 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 ) Eisenia foetida4 = Verified data |
Low | ||||||||
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Aquatic ecotoxicology |
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0.62 | 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 |
Moderate | ||||||||
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0.41 | 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 |
Moderate | ||||||||
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> 0.012 | 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 |
Moderate | ||||||||
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0.025 | 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 ) Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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0.015 | 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 ) Raphidocelis subcapitata4 = Verified data |
Moderate | ||||||||
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General |
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Eliminated through hepatic metabolism, followed by biliary and faecal excretion | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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No information available |
Handling issues |
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No information available | |||
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Store at or below 25 DegC |
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lubabegron fumerate | ||
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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 |