| Pythium oligandrum strain B301 |

Last updated: 08/02/2026
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(Not known by any other names) |
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 fungal parasite widespread in nature, which can be used to control a wide range of soil-borne fungal pathogens |
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Soil pathogens including Botrytis; Fusarium; Gaeumannomyce; Ophiostoma; Phialophora; Phoma; Phythopthora; Pseudocercosporella; Pythium; Sclerotinia; Verticillium |
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Oilseed rape; Wheat; Spring barley; Grapes; Glasshouse vegetables |
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Efficiacy supported by field trials |
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Filamentous. Colonises the rhizosphere of treated plants. Accession number I-5180. Life cycle has two phases. Firstly, the asexual production of sporangia and secondly, a sexual phase generating oospores |
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Class: Oomycetes; Order: Perensporales; Family: Pythiaceae. NB Orginally thought to be fungal now assigned to the Chromista Kingdom |
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Not approved |
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- |
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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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Approved |
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Belgium |
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10/02/2035 |
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No |
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Yes |
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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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Not applicable |
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No |
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Fungicide |
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Systemic resistance inducer/elicitor |
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Micro-organism |
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1.0E+07 oospores per gram |
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EFSA 2024 dossier: tryptamine metabolite < 0.41 g kg⁻¹ |
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Natural |
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Multiple routes: mycoparasitism, outcompetes pathogenic soil fungi for space and nutrients and also stimulates crop resistance to attack via the production of auxin-like substances. |
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Naturally occuring in soils and globally widespread. First isolated from vineyard soils in Bordeaux region, France. |
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Crop protection |
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Botrytis; Fusarium; Gaeumannomyce; Ophiostoma; Phialophora; Phoma; Phythopthora; Pseudocercosporella; Pythium; Sclerotinia; Verticillium |
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Oilseed rape; Wheat; Spring barley; Grapes; Glasshouse vegetables |
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Suitable for use in all farming systems where approved for use in that country |
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936 |
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Pythium oligandrum strain B301 |
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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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Not applicable |
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Not applicable |
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Not applicable |
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BM02 |
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Fungus |
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Novel |
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2011, first isolated |
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Usually supplied as a wettable powder. A single application is usually sufficient for an entire season. |
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Commercial production of Pythium oligandrum involves cultivating its oospores under controlled fermentation conditions. Some companies have pioneered industrial-scale production using co-products derived from sugarcane molasses as a nutrient base. The process includes optimising growth conditions to maximise oospore yield and viability, employing advanced techniques such as digital PCR and flow cytometry to quantify and ensure the integrity of the spores. Viability is further assessed using staining methods like Trypan Blue combined with plasmolysis, ensuring that the final product contains potent and effective spores. |
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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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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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| Known soil and groundwater metabolites |
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None
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tryptamine Note: Toxicologically relevant |
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Human, Rodent, Plant, Fungi |
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| Terrestrial ecotoxicology |
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> 2.98 x 1006 |
Colinus virginianus as oospores/kg BW/day |
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> 491 |
P5 P = Other non-EU, UK or US Governments and Regulators 5 = Verified data used for regulatory purposes Apis mellifera |
Low |
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> 105 |
P5 P = Other non-EU, UK or US Governments and Regulators 5 = Verified data used for regulatory purposes Apis mellifera |
Low |
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> 5.0 x 1004 |
Oncorhynchus mykiss as oospores/kg BW/day |
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> 5.0 x 1004 |
Daphnia magna as oospores/kg BW/day |
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1.30 x 1006 |
Raphidocelis subcapitata as oospores/kg BW/day |
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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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No data |
No data for acute and chronic mammals |
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298000 |
Worst case of 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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2.1 |
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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500 |
Worst case of temperate acute and chronic fish |
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500 |
Worst case of temperate acute and chronic aquatic invertebrates |
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130000 |
Worst case of free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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Not applicable |
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None allocated |
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None allocated |
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None allocated |
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None allocated |
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Negligible risk to bystanders for proposed uses |
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Negligible risk to operators for proposed uses |
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| Carcinogen |
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Endocrine disruptor |
XNo, known not to cause a problem |
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 |
XNo, known not to cause a problem |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
XNo, known not to cause a problem |
XNo, known not to cause a problem |
XNo, known not to cause a problem |
| Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
XNo, known not to cause a problem |
?Possibly, status not identified |
?Possibly, status not identified |
| Eye irritant |
Phototoxicant |
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?Possibly, status not identified |
No data found |
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Micro-organisms may provoke sensitising reactions |
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No information available |
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Not listed (Not listed) |
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Pythium oligandrum strain B301 |
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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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