Monensin A |
![]() Last updated: 08/09/2025 |
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(Also known as: monensic acid) |
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A broad spectrum ionophone veterinary antibotic isolated from Streptomyces cinnamonensis and usually used as the sodium salt of monensin factor A. S. cinnamonensis produces monensin A and monensin B that differ only in the side chain at C-16. | |
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Used as a coccidiostat drug as well as a growth promotor | |
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Poultry; Cattle; Goats |
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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Monensin has four isomers labeled A, B, C, and D. The A isomer is the major component, making up about 98% of the mixture | |
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C₃₆H₆₂O₁₁ | |
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CCC1(CCC(O1)C2(CCC3(O2)CC(C(C(O3)C(C)C(C(C)C(=O)O)OC)C)O)C)C4C(CC(O4)C5C(CC(C(O5)(CO)O)C)C)C | |
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CC[C@]1(CC[C@@H](O1)[C@]2(CC[C@@]3(O2)C[C@@H]([C@H]([C@H](O3)[C@H](C)[C@@H]([C@@H](C)C(=O)O)OC)C)O)C)[C@@H]4[C@@H](C[C@H](O4)[C@@H]5[C@H](C[C@H]([C@@](O5)(CO)O)C)C)C | |
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GAOZTHIDHYLHMS-GDMSFIFLSA-N | |
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InChI=1S/C36H62O11/c1-10-34(31-20(3)16-26(43-31)28-19(2)15-21(4)36(41,18-37)46-28)12-11-27(44-34)33(8)13-14-35(47-33)17-25(38)22(5)30(45-35)23(6)29(42-9)24(7)32(39)40/h19-31,37-38,41H,10-18H2,1-9H3,(H,39,40)/t19-,20+,21+,22+,23+,24+,25-,26-,27+,28-,29-,30-,31-,33+,34-,35+,36-/m0/s1 | |
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Yes |
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Common Name | Relationship | Link |
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Monensin monohydrate | Hydrate | ![]() |
General status |
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Antibiotic, Antibacterial, Coccidiostat, Feed additive, Growth promotor | |
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Polyether (ionophore) | |
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Natural | |
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A protein transport inhibitor | |
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[Intracellular protein transport, Blocker] | |
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17090-79-8 | |
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241-154-0 | |
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Antiparasitic products, insecticides & repellents: Antiprotozoals | |
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QP51AH03 | |
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No | |
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Allowed substance (Table 1: Bovine) | |
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670.87 | |
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4-[2-[5-ethyl-5-[5-[6-hydroxy-6-(hydroxymethyl)-3,5-dimethyl-oxan-2-yl]-3-methyl-oxolan-2-yl]oxolan-2-yl]- 9-hydroxy-2,8-dimethyl-1,6-dioxasp iro[4.5]dec-7-yl]-3-methoxy-2-methyl-pentanoic acid | |
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White crystalline solid | |
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Commercial |
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Current | |||||||||
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1979, first synthesised; mid-1980s, registered for vet use USA | |||||||||
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Monensin A is produced through a microbial fermentation process using Streptomyces cinnamonensis, a soil-dwelling actinomycete. The biosynthesis begins with the cultivation of this microorganism in a nutrient-rich medium, where it naturally synthesises monensin as a secondary metabolite. The fermentation broth is then treated with sodium hydroxide to convert the compound into its sodium salt form, enhancing stability and solubility. After pH adjustment, calcium carbonate is added to aid in precipitation, followed by filtration to separate the solid monensin-rich pulp. The resulting filter cake is then dried to yield a concentrated monensin premix, which can be further processed or formulated for use in veterinary applications. | |||||||||
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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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4.8 | 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 |
Low | ||||||||
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104 | 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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5.75 X 1002 | Calculated | - | |||||||
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2.76 | 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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6.65 | 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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4.27 X 10-18 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Low volatility | ||||||||
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Monensin is found in turkey excreta and so may be introduced into soil by use of turkey litter as a soil amendment. Monensin is extensively metabolied by cattle |
Degradation |
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7.4 | R3 R = Peer reviewed scientific publications 3 = Unverified data of known source |
Non-persistent | |||||||
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General literature: 1ppm soil conc, only trace remained after 20 days (R4) | ||||||||||
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5.8 | R3 R = Peer reviewed scientific publications Soil & cattle manure3 = Unverified data of known source |
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43 | 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 |
Stable | |||||||
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Stable | 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 |
Stable | |||||||
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Stable at all relevant environmental pH values | ||||||||||
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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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Fate indices |
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Known soil and groundwater metabolites |
None
Other known metabolites |
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monensin methyl ester | MME | - | - | ||||
monensin decyl ester | MDE | - | - |
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Terrestrial ecotoxicology |
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100 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Moderate | ||||||||
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264.2 | 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 ) Eisenia foetida3 = Unverified data of known source |
Moderate | ||||||||
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10 | R4 R = Peer reviewed scientific publications 4 = Verified data |
Moderate | ||||||||
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Aquatic ecotoxicology |
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9 | R4 R = Peer reviewed scientific publications Oncorhynchus mykiss as sodium salt4 = Verified data |
Moderate | ||||||||
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10.7 | R4 R = Peer reviewed scientific publications Daphnia magna as sodium salt4 = Verified data |
Moderate | ||||||||
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0.98 | 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 ) Raphidocelis subcapitata3 = Unverified data of known source |
Moderate | ||||||||
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0.055 | 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 ) Raphidocelis subcapitata3 = Unverified data of known source |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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100 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Moderate | ||||||||
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Intraperitoneal LD₅₀ = 15 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
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Excreted rapidly in the faeces and urine | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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May cause pulmonary edema May cause gastroinstinal and renal function problems Possible cardiac, thyroid, kidney and adrenal toxicant |
Handling issues |
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When heated to decomposition it emits acrid smoke & irritating fumes | |||
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Not listed (Not listed) | |||
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UN2811 | |||
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monensin A | ||
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monensina | ||
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Record last updated: | 08/09/2025 |
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 |