Valinomycin |
![]() Last updated: 09/09/2025 |
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(Also known as: Antibiotic N-329 B) |
Hazard alerts |
The following alerts are based on the data in the tables below. An absence of an alert does not imply the substance has no implications for human health, biodiversity or the environment but just that we do not have the data to form a judgement. These hazard alerts do not take account of usage patterns or exposure, thus do not represent risk.
Environmental fate | Ecotoxicity | Human health |
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A potent antibiotic active against gram-positive bacteria, plant pathogenic fungi and shown to also have antiviral properties, Reported to be a potent agent against SARS-CoV in humans | |
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Grey mold Botrytis cinerea; Growth | |
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Cucumbers; Cattle; Sheep | |
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GB regulatory status |
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Not approved | ||
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Not applicable | ||
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No UK approval for use as a plant protection agent |
EC Regulation 1107/2009 (repealing 91/414) |
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Not approved | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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Additional information |
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Chemical structure |
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Valinomycin exhibits stereoisomerism, specifically optical isomerism, due to the presence of multiple chiral centres in its cyclic structure. It is a cyclododecadepsipeptide, composed of alternating units of D-valine, L-valine, D-α-hydroxyisovaleric acid, and L-lactic acid, forming a 36-membered ring. Each amino acid and hydroxy acid unit contributes one or more chiral centres, resulting in a highly stereochemically complex molecule. | |
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C₅₄H₉₀N₆O₁₈ | |
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CC1C(=O)NC(C(=O)OC(C(=O)NC(C(=O)OC(C(=O)NC(C(=O)OC(C(=O)NC(C(=O)OC(C(=O)NC(C(=O)OC(C(=O)NC(C(=O)O1)C(C)C)C(C)C)C(C)C)C)C(C)C)C(C)C)C(C)C)C)C(C)C)C(C)C)C(C)C | |
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No data | |
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FCFNRCROJUBPLU-GGUWDUSBSA-N | |
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InChI=1S/C54H90N6O18/c1-22(2)34-49(67)73-31(19)43(61)55-38(26(9)10)53(71)77-41(29(15)16)47(65)59-36(24(5)6)51(69)75-33(21)45(63)57-39(27(11)12)54(72)78-42(30(17)18)48(66)60-35(23(3)4)50(68)74-32(20)44(62)56-37(25(7)8)52(70)76-40(28(13)14)46(64)58-34/h22-42H,1-21H3,(H,55,61)(H,56,62)(H,57,63)(H,58,64)(H,59,65)(H,60,66 | |
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Yes |
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Common Name | Relationship | Link |
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valinomycin | - | ![]() |
General status |
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Insecticide; Nematicide; Fungicide; Veterinary substance | |
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Ionophore drug; Micro-organism derived drug | |
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Natural | |
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Induces cell death, increases the transport of potassium ions across cell membranes | |
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Produced by the bacterium Streptomyces fulvissimus | |
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Crop protection; Animal welfare; Animal production | |
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Botrytis cinerea | |
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Cucumbers; Cattle; Sheep | |
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2001-95-8 | |
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217-896-6 | |
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1111.32 | |
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cyclo(D-α-hydroxyisovaleryl-D-valyl-L-lactoyl-L-valyl-D-α-hydroxyisovaleryl-D-valyl-Lactoyl-L-valyl-D-α-hydroxyisovaleryl-D-valyl-L-lactoyl-L-valyl) | |
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1,7,13,19,25,31-Hexaoxa-4,10,16,22,28,34-hexaazacyclohexatriacontane-2,5,8,11,14,17,20,23,26,29,32,35-dodecone, 12,24,36-trimetyl-3,6,9,15,18,21,27,30,33-nonakis(1-methylethyl)- | |
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Not applicable | |
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Not applicable | |
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Not known | |
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Not applicable | |
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White solid |
Commercial |
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Novel | |||
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1955, first isolated; 1960, first recognised as a potassium-selective ionophore | |||
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Valinomycin is produced through microbial fermentation or recombinant biosynthesis, typically using Streptomyces fulvissimus or engineered strains like Escherichia coli. In recombinant systems, the biosynthetic genes encoding nonribosomal peptide synthetases (NRPSs) are introduced into the host, enabling it to assemble valinomycin from precursors such as D- and L-valine, D-α-hydroxyisovaleric acid, and L-lactic acid. Production is optimised using fed-batch cultivation, where glucose is gradually supplied to maintain controlled growth and maximize yield. Parameters like pH, dissolved oxygen, and cell density are closely monitored, and enzyme-based glucose release systems are often used to fine-tune the process. After fermentation, valinomycin is extracted using organic solvents and purified via chromatographic techniques. | |||
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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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172 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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3.09 X 1004 | Calculated | - | |||||||
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4.49 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
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1.060 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Degradation |
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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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Known metabolites |
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Terrestrial ecotoxicology |
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4.0 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
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Aquatic ecotoxicology |
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General |
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High (class III) | - | - | ||||||||
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4.0 | E3 E = Manufacturers safety data sheets Rat3 = Unverified data of known source |
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5.0 | E3 E = Manufacturers safety data sheets Rabbit3 = Unverified data of known source |
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Intraperitoneal LD₅₀ = 39 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Mouse3 = Unverified data of known source |
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Subcutaneous LD₅₀ = 4.14 mg kg⁻¹ | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Mouse3 = Unverified data of known source |
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Data is scarce but likely cleared through hepatic metabolism followed by biliary excretion | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Health issues |
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Very toxic by ingestion, dermal contact and inhalation Possible cardiovascular system, eyes and nervous system toxicant |
Handling issues |
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IMDG Transport Hazard Class 6.1 May emit toxic fumes when heated Corrosive |
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Health: H300, H310 | |||
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Not listed (Not listed) | |||
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UN2811 | |||
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Packaging Group I (great danger) | |||
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valinomycin | ||
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Record last updated: | 09/09/2025 |
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 |