| Mildiomycin (Ref: AR-1F1870) |

Last updated: 08/02/2026
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(Also known as: antibiotic B-98891; TF-138) |
The following Pesticide Hazard Tricolour (PHT) 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. The alerts for Highly Hazardous Pesticides (HHPs) are based on applying the FAO/WHO (Type 1) and the PAN (Type II) criteria to PPDB data. Further details on the HHP indicators are given in the tables below. Neither the PHT nor the HHP hazard alerts take account of usage patterns or exposure, thus they do not represent risk.
| PHT: Environmental fate |
PHT: Ecotoxicity |
PHT: Human health |
Highly Hazardous Pesticide |
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A peptidyl nucleoside antibiotic with strong activity against plant powdery mildew disease. |
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Powdery mildew |
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Ornamentals |
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- |
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- |
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- |
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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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Not applicable |
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Not applicable |
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Not applicable |
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No |
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ATAustria |
BEBelgium |
BGBulgaria |
CYCyprus |
CZCzech Republic |
DEGermany |
DKDenmark |
EEEstonia |
ELGreece |
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ESSpain |
FIFinland |
FRFrance |
HRCroatia |
HUHungary |
IEIreland |
ITItaly |
LTLithuania |
LULuxembourg |
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LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
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ISIceland |
NONorway |
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Mildiomycin is a chiral molecule |
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C₁₉H₃₀N₈O₉ |
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C1=CC(OC(C1NC(=O)C(CO)N)C(CC(CN=C(N)N)O)(C(=O)O)O)N2C=C(C(=NC2=O)N)CO |
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- |
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QKJJCZYFXJCKRX-UHFFFAOYSA-N |
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InChI=1S/C19H30N8O9/c20-10(7-29)15(31)25-11-1-2-12(27-5-8(6-28)14(21)26-18(27)34)36-13(11)19(35,16(32)33)3-9(30)4-24-17(22)23/h1-2,5,9-13,28-30,35H,3-4,6-7,20H2,(H,25,31)(H,32,33)(H2,21,26,34)(H4,22,23,24) |
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Yes |
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Fungicide |
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Micro-organism derived substance |
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- |
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- |
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Natural |
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Thought to inhibit fungal protein biosynthesis |
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A substance produced naturally by the soil actinomycetes Streptoverticillium rimofaciens strain B-98891 |
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Crop protection |
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Powdery mildew |
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Ornamentals |
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- |
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67527-71-3 |
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614-077-9 |
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- |
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- |
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- |
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514.49 |
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- |
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4-amino-1-[4-[[(S)-2-amino-3-hydroxy-1-oxopropyl]amino]-9-guanidino-6-carboxy-2,3,4,7,9-pentadeoxy-a-L-talo-nona-2-enopyranosyl]-5-(hydroxymethyl)pyrimidin-2(1H)-one |
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(S)-4-amino-1-[4-[(2-amino-3-hydroxy-1-oxopropyl)amino]-9-[(aminoiminomethyl)amino]-6-C-carboxy-2,3,4,7,9-pentadeoxy-a-L-talo-non-2-enopyranosyl]-5-(hydroxymethyl)-2(1H)-pyrimidinone |
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| UK Poisons List Order 1972 |
Rotterdam Convention |
Montreal Protocol |
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| Stockholm Convention |
OSPAR |
EU Water Framework Directive |
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- |
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- |
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- |
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- |
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- |
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Not applicable |
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Not applicable |
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Not applicable |
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- |
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- |
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Hygroscopic white solid |
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- |
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1979, fungal properties first described |
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- Sumitomo Chemical Co.
- Takeda Pharmaceutical
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- Milanecin
- Mildiomycin powder
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Usually formulated as a wettable powder and used as a foliar spray |
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Mildiomycin is produced commercially through the cultivation of specific microorganisms typically belonging to the Actinomycetes family, in a suitable culture medium. The microorganism is grown, under controlled conditions, in a fermentation broth that contains necessary nutrients. After fermentation, mildiomycin is extracted from the culture medium and purified to obtain the final product |
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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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- |
- |
- |
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- |
- |
- |
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>300 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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- |
- |
- |
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- |
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- |
- |
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- |
- |
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- |
- |
- |
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- |
- |
- |
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2.8 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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| Weak base, PKa(2) = 4.3, PKa(3) = 7.2 |
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- |
- |
- |
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- |
- |
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- |
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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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None
| Terrestrial ecotoxicology |
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> 4120 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Rat |
Low |
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- |
- |
- |
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- |
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- |
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- |
- |
- |
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- |
- |
- |
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> 100 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Apis mellifera |
Low |
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> 100 |
Apis mellifera |
Low |
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- |
- |
- |
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- |
- |
- |
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- |
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| - |
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- |
- |
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- |
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- |
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- |
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- |
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> 40 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Cyprinus carpio |
Moderate |
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- |
- |
- |
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- |
- |
- |
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> 20 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Daphia pulex |
Moderate |
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- |
- |
- |
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- |
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- |
- |
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- |
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- |
- |
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- |
- |
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8.05 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Raphidocelis subcapitata |
Moderate |
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- |
- |
- |
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- |
- |
- |
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- |
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- |
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| Regulatory Threshold Levels (RTLs) |
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Note: These RTLs have been calculated using the regulatory approach used in the European Union and based on ecotoxocity values in the PPDB.
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412 |
Worst case of acute and chronic mammals |
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No data |
No data for acute and chronic birds |
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No data |
No data for acute and chronic earthworms |
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No data |
No data for non-target plants vegetative vigour and seedling emergence |
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2 |
Worst case of contact and oral honeybees |
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No data |
No data for parasitic wasps and predatory mites |
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0.4 |
Worst case of temperate acute and chronic fish |
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0.2 |
Worst case of temperate acute and chronic aquatic invertebrates |
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0.805 |
Worst case of free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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High (class III) |
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- |
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> 4120 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Rat |
Low |
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- |
- |
- |
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- |
- |
- |
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> 5000 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source Rat |
- |
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- |
- |
- |
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Intraperitoneal LD₅₀ = 679 mg kg⁻¹ |
Rat |
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| Intravenous LD₅₀ = 500 mg kg⁻¹ |
Rat |
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- |
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- |
- |
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- |
- |
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| Carcinogen |
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Endocrine disruptor |
| No data found |
A0 A = Chromosome aberration (EFSA database) 0 = No data ; B0 B = DNA damage/repair (EFSA database) 0 = No data ; C0 C = Gene mutation (EFSA database) 0 = No data ; D0 D = Genome mutation (EFSA database) 0 = No data ; E3 E = Unspecified genotoxicity type (miscellaneous data source) 3 = Negative |
No data found |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
| No data found |
No data found |
No data found |
| Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
| No data found |
XNo, known not to cause a problem |
?Possibly, status not identified |
| Eye irritant |
Phototoxicant |
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XNo, known not to cause a problem |
No data found |
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No further information available |
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Hygroscopic |
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- |
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Not listed (Not listed) |
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mildiomycin |
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| Record last updated: |
08/02/2026 |
| 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 |
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