Laidlomycin propionate potassium |
![]() Last updated: 16/09/2025 |
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(Also known as: potassium laidlomycin propanoate) |
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A semi-synthetic variant of laidlomycin which is a natural product found in Streptomyces and used as a veterinary antibiotic for control of gram-positive bacteria | |
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Used as a poultry coccidiostat and as a feed additive to improve feed efficiency in cattle | |
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Poultry; Cattle |
Approval status |
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Not approved | |
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Not approved |
Chemical structure |
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Laidlomycin propionate potassium exhibits extensive stereoisomerism due to its complex polyether structure, which contains 17 defined chiral centres across multiple fused and spirocyclic rings. These chiral centres give rise to a single, highly specific stereoisomer that is biologically active as an ionophore antibiotic. | |
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C₄₀H₆₅KO₁₃ | |
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CCC(=O)OCC1(C(CC(C(O1)C2CC(C(O2)C3(CCC(O3)C4(CCC5(O4)CC(C(C(O5)C(C)C(C(C)C(=O)[O-])OC(=O)CC)C)O)C)C)C)C)C)O.[K+] | |
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CCC(=O)OC[C@]1([C@@H](C[C@@H]([C@H](O1)[C@H]2C[C@@H]([C@@H](O2)[C@@]3(CC[C@@H](O3)[C@@]4(CC[C@@]5(O4)C[C@@H]([C@H]([C@H](O5)[C@@H](C)[C@H]([C@H](C)C(=O)[O-])OC(=O)CC)C)O)C)C)C)C)C)O.[K+] | |
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OXNOQXLCECXEBU-QGMAIPBJSA-M | |
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InChI=1S/C40H66O13.K/c1-11-30(42)47-20-40(46)23(5)17-21(3)32(52-40)28-18-22(4)35(48-28)38(10)14-13-29(50-38)37(9)15-16-39(53-37)19-27(41)24(6)34(51-39)25(7)33(26(8)36(44)45)49-31(43)12-2;/h21-29,32-35,41,46H,11-20H2,1-10H3,(H,44,45);/q;+1/p-1/t21-,22-,23+,24+,25-,26-,27-,28+,29+,32-,33+,34-,35+,37-,38-,39+,40-;/m0. | |
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Yes |
General status |
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Medicinal drug, Antibiotic | |
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Ionophore | |
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Semi-synthetic | |
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Inhibits bacterial protein synthesis by binding to the 23S RNA of the 50S subunit of the bacterial ribosome | |
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[23S ribosomal RNA, Binder], [Streptococcus, Inhibitor], [Ion transport, Activator] | |
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84799-02-0 | |
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23674236 | |
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Ionophores against coccidiosis | |
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QP51BB | |
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No | |
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793.0 | |
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potassium;(2S,3R,4R)-4-[(2S,5R,7S,8R,9S)-7-hydroxy-2-[(2R,5S)-5-[(2R,3S,5R)-5-[(2S,3S,5R,6R)-6-hydroxy-3,5-dimethyl-6-(propanoyloxymethyl)oxan-2-yl]-3-methyloxolan-2-yl]-5-methyloxolan-2-yl]-2,8-dimethyl-1,10-dioxaspiro[4.5]decan-9-yl]-2-methyl-3-propanoyloxypentanoate | |
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Off-white to grey coloured granular solid |
Commercial |
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Current | |||
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1980s, discovered; 1994, first approvals USA; 2000s, commercial expansion | |||
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Usually formulated for incorporation into Type B and Type C medicated feed | |||
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The commercial production of laidlomycin propionate potassium begins with the fermentation of Streptoverticillium eurocidicum. After fermentation, the crude antibiotic is extracted and purified using solvent extraction and chromatographic techniques to isolate the laidlomycin base. This base is then chemically modified through esterification with propionic acid to form laidlomycin propionate, enhancing its lipophilicity and stability. The final step involves neutralisation with potassium hydroxide, yielding the potassium salt form: laidlomycin propionate potassium. | |||
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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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314 | 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 |
Moderate | ||||||||
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160 | 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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160 | 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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5.5 | 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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as laidlomycin | |||||||||||
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Substance may enter the environment via the faeces of treated animals or by leaching from spilt medicated feed. |
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18 | 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 ) Extensive biotransformation3 = 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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29.4 | 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 |
Slightly mobile | |||||||
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3532 | ||||||||||
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USEPA data: Kd range 4.09-93.2 mL g⁻¹, Koc range 390-11000 mL.g, Soils=4 | ||||||||||
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Fate indices |
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Known metabolites |
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Terrestrial ecotoxicology |
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63 | 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 ) Rat3 = Unverified data of known source |
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4.0 | 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 ) Rat3 = Unverified data of known source |
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Aquatic ecotoxicology |
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> 9.5 | 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 ) Lepomis macrochirus3 = Unverified data of known source |
Moderate | ||||||||
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239 | 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 |
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General |
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63 | 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 ) Rat3 = Unverified data of known source |
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Elimination is both urinary and via bile | 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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Health issues |
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Possible heart, liver and CNS toxicant |
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Avoid creation of dust Not explosive or oxidising |
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Not regulated | |||
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laidlomycin propionate potassium | ||
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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 |