| Trichoderma asperellum strain T34 |

Last updated: 08/02/2026
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(Also known as: Trichoderma harzianum) |
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 biological fungicide used to control various soil-borne fungal pathogens |
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Soil-borne pathogens including Fusarium wilt disease (caused by Fusarium oxysporium f. Sp. Dianthi), damping-off and rot (especially Pythium species. |
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Tomatoes; Cucumbers; Melon; Pumpkin; Zucchini; Sweet peppers; Aubergine, Sunflower; Maize; Soybean; Ornamentals including carnations. |
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- |
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Mycelium consist of irregular, filamentous branched hypae. It has a typical growth pattern for imperfect fungi with only asexual reproduction. Good ability to colonise plant roots. Optimum growth at <36 DegC. No growth expected above this temperature. |
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Class: Sordariomycetes; Order: Hypocreales; Family: Hypocreaceae |
| EC Regulation 1107/2009 (repealing 91/414) |
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Approved |
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Sweden/Italy |
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31/10/2027 |
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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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✓ |
✓ |
✓ |
✓ |
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ESSpain |
FIFinland |
FRFrance |
HRCroatia |
HUHungary |
IEIreland |
ITItaly |
LTLithuania |
LULuxembourg |
| ✓ |
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✓ |
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✓ |
✓ |
✓ |
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LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
| ✓ |
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✓ |
✓ |
✓ |
✓ |
✓ |
✓ |
✓ |
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ISIceland |
NONorway |
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Not applicable |
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- |
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No |
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Fungicide |
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Micro-organism |
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- |
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EFSA 2024: No relevant impurities |
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Natural |
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Inhibits the growth of pathogenic fungi by competing for nutrients and invasion sites. Also thought to include mycoparasitism and by instigating plant metabolic changes. |
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Originally isolated from a natural suppressive compost-peat mix. Trichoderma spp. are present in most soils and many other media including decaying wood and vegetable matter in both temperate and tropical areas. |
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Crop protection usually in a protected environment such as a glasshouse |
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Soil-borne pathogens including Fusarium wilt disease (caused by Fusarium oxysporium f. Sp. Dianthi), damping-off and rot |
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Tomatoes; Cucumbers; Ornamentals including carnations. |
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Suitable for use in all farming systems where approved for use in that country |
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- |
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941 |
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Trichoderma asperellum strain 34 |
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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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Not applicable |
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Not applicable |
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Not applicable |
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BM02 |
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- |
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Fungus |
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Current |
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1999, First described; 2001, first isolated |
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- Biocontrol Technologies SL
- Fargro Limited
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Usually supplied as wettable microgranules and powders and typically applied as a soil drench |
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Trichoderma asperellum is produced commercially through a controlled fermentation process. The specific strain is isolated from natural sources and identified using molecular techniques to ensure the correct species. The fungus is grown in large fermentation tanks under controlled conditions. Once the desired growth is achieved, the fungal biomass and spores are harvested. This can be done using filtration or centrifugation methods. The harvested product is then formulated into a stable form. |
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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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None
| Terrestrial ecotoxicology |
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> 1.1 x 1008 |
Rat as CFU/rat |
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1.0 x 1008 |
Colinus virginianus as CFU/bird |
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> 7.80 x 1006 |
Eisenia foetida as CFU/ha |
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7.80 x 1006 |
Eisenia foetida as CFU/ha |
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1.0 x 1005 |
Apis mellifera as CFU/bee |
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1.11 x 1006 |
Pseudokirchneriella subcapitata 96 hr as CFU/L |
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Non-toxic |
No adverse effects identified or expected |
Non-toxic |
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> 2.3 x 1012 |
Aphidius rhopalosiphi |
Low |
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> 2.3 x 1012 |
Typhlodromus pyri |
Low |
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> 9.6 x 1008 |
Oncorhynchus mykiss as CFU/L |
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9.6 x 1008 |
Oncorhynchus mykiss as CFU/L |
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< 7.18 x 1007 |
daphnia magna as CFU/L |
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1.0 x 1009 |
Lemna gibba as CFU/L |
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- |
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4.3 x 1007 |
Raphidocelis subcapitata as CFU/L |
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3.3 x 1006 |
Raphidocelis subcapitata as CFU/L |
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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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11000000 |
Worst case of acute and chronic mammals |
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10000000 |
Worst case of acute and chronic birds |
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1560000 |
Worst case of 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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2000 |
Worst case of contact and oral honeybees |
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1150000000000 |
Worst case of parasitic wasps and predatory mites |
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9600000 |
Worst case of temperate acute and chronic fish |
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718000 |
Worst case of temperate acute and chronic aquatic invertebrates |
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330000 |
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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> 1.1 x 1008 |
Rat as CFU/rat |
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> 1.1E+07 |
Rat as CFU/rat |
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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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PPC advised due to the potential sensitising risk |
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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 |
XNo, known not to cause a problem |
?Possibly, status not identified |
| Eye irritant |
Phototoxicant |
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✓Yes, known to cause a problem |
No data found |
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May cause sensitisation by inhalation or skin contact |
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No information available |
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Not listed (Not listed) |
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Trichoderma asperellum strain T34 |
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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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