Monensin sodium |
![]() Last updated: 16/09/2025 |
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(Also known as: monensic acid, sodium salt) |
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A broad spectrum ionophone veterinary antibotic isolated from Streptomyces cinnamonensis | |
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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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Not approved | |
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Not approved |
Chemical structure |
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Monensin, itself, 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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C₃₆H₆₁O₁₁Na | |
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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.[Na+] | |
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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.[Na+] | |
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XOIQMTLWECTKJL-PDHYURILSA-M | |
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InChI=1S/C36H62O11.Na/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);/q;+1/p-1/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 | Parent | ![]() |
General status |
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Antibiotic, Antibacterial, Coccidiostat, Feed additive, Growth promotor | |
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Polyether (ionophore) | |
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>98% | |
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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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22373-78-0 | |
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244-941-7 | |
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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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692.86 | |
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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, sodium salt | |
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Light brown to white crystalline solid whith characteristic odour |
Commercial |
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Current | |||
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1979, first synthesised; Mid 1980s, registered for vet use USA | |||
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Usually supplied as a premix or feed additive | |||
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Monensin sodium is produced through a microbial fermentation process using the bacterium Streptomyces cinnamonensis. The process begins with cultivating the strain in nutrient-rich media under aerobic conditions, where it biosynthesises monensin as a secondary metabolite. After fermentation, the broth is treated with NaOH to convert monensin into its sodium salt, then extracted using organic solvents, concentrated, and purified, often via chromatography and crystallisation, to yield high-purity monensin sodium. | |||
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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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63.0 | 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 ) 3 = Unverified data of known source |
Moderate | ||||||||
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25000 | E3 E = Manufacturers safety data sheets Ethanol3 = Unverified data of known source |
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50000 | E3 E = Manufacturers safety data sheets Methanol3 = Unverified data of known source |
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25000 | E3 E = Manufacturers safety data sheets Chloroform3 = Unverified data of known source |
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267 | 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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2.69 X 1005 | Calculated | - | |||||||
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5.43 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
High | ||||||||
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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 metabolised by cattle |
Degradation |
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7.5 | 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-persistent | |||||||
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USEPA data: DT₅₀ 7.5 days in soil without manure, and 7.4 days with cattle manure (F4). General literature: 1ppm soil conc, only trace remained after 20 days (R4) | ||||||||||
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7.4 | 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 ) soil & cattle manure in field; DT₅₀ 5.8 days for soil & cattle manure in greenhouse R33 = Unverified data of known source |
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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 environmentally relevant 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 | - | - | ||||
O-desmethyl monensin Note: Significantly less biologically active than parent |
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Terrestrial ecotoxicology |
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29 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
High | ||||||||
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85.7 | 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 ) Colinus Virginianus3 = Unverified data of known source |
High | ||||||||
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980 mg kg bw⁻¹ day⁻¹ | 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 ) Colinus Virginianus3 = Unverified data of known source |
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> 500 | 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 ) Enchytraeus crypticus4 = Verified data |
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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9.0 | R4 R = Peer reviewed scientific publications Oncorhynchus mykiss4 = Verified data |
Moderate | ||||||||
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10.7 | R4 R = Peer reviewed scientific publications Daphnia magna4 = Verified data |
Moderate | ||||||||
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General |
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High (class III) | - | - | ||||||||
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29 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
High | ||||||||
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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 Contact with metals may evolve flammable hydrogen gas IMDG Transport Hazard Class 6.1 |
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Not listed (Not listed) | |||
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UN2811 | |||
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Pachaging Group III (minor danger) | |||
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monensin sodium | ||
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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 |