Bacillus pumilus strain QST 2808

Bacillus pumilus strain QST 2808	Last updated: 25/08/2025
(Not known by any other names)

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
		Human health Low alert

GENERAL INFORMATION

Description

A gram-positive bacterium used to control a wide variety of plant fungal diseases

Example pests controlled

molds; Mildews; Blights; Rusts and Phytophthora ramorum which is the oomycete that causes sudden oak death syndrome

Example applications

Many food and non-food crops; Trees; Ornamentals

Efficacy & activity

Appearance and life cycle

Cells are 3.5-5 um long and around 1.5um thick and opaque in colour.

Taxonomic classification

Class: Bacilli; Order: Bacillales; Family: Bacillaceae

GB regulatory status

GB COPR regulatory status

Approved

Date COPR inclusion expires

31/08/2025

GB LERAP status

None

EC Regulation 1107/2009 (repealing 91/414)

EC Regulation 1107/2009 status

Not approved

Dossier rapporteur/co-rapporteur

Italy/Netherlands

Date EC 1107/2009 inclusion expires

Not applicable

EU Candidate for substitution (CfS)

Listed in EU database

Yes

Approved for use (✓) under EC 1107/2009 in the following EU Member States

ATAustria	BEBelgium	BGBulgaria	CYCyprus	CZCzech Republic	DEGermany	DKDenmark	EEEstonia	ELGreece

ESSpain	FIFinland	FRFrance	HRCroatia	HUHungary	IEIreland	ITItaly	LTLithuania	LULuxembourg

LVLatvia	MTMalta	NLNetherlands	PLPoland	PTPortugal	RORomania	SESweden	SISlovenia	SKSlovakia

Approved for use (✓) under EC 1107/2009 by Mutual Recognition of Authorisation and/or national regulations in the following EEA countries

ISIceland	NONorway

Additional information

Known to be also used in the following countries

USA, South Korea

Chemical structure

Isomerism

Not applicable

Chemical formula

Canonical SMILES

Isomeric SMILES

International Chemical Identifier key (InChIKey)

International Chemical Identifier (InChI)

2D structure diagram/image available?

General status

Biopesticide type

Fungicide

Substance groups

Micro-organism

Minimum active substance purity

Known relevant impurities

Substance origin

Natural

Mode of action

Inhibits fungal pathogen development and activates plants immune system. Has curative and preventative properties.

Substance source

A common bacterium found in both soil and water, the strain was originally isolated from a soil sample collected from Micronesia, 1998

Uses

Crop protection; Nurseries pest control; Forestry; Landscape management

Target pests

Moulds; Mildews; Blights; Rusts and Phytophthora ramorum which is the oomycete that causes sudden oak death syndrome

Target host

Many food and non-food crops; Trees; Ornamentals

Farming system suitability

Suitable for use in all farming systems where approved for use in that country

CAS RN

EC number

CIPAC number

US EPA chemical code

006485

PubChem CID

Molecular mass

Chemical name

Bacillus pumilus strain QST 2808

PIN (Preferred Identification Name)

IUPAC name

CAS name

Forever chemical

Other status information

Relevant Environmental Water Quality Standards

Herbicide Resistance Class (HRAC MoA class)

Not applicable

Herbicide Resistance Class (WSSA MoA class)

Not applicable

Insecticide Resistance Class (IRAC MoA class)

Not applicable

Fungicide Resistance Class (FRAC MOA class)

BM02

Examples of recorded resistance

Physical state

Bacterium

Commercial

Property

Value

Availability status

Current

Introduction & key dates

1998, first isolated

Example manufacturers & suppliers of products using this active now or historically

AgraQuest Inc

Example products using this active

QRD 288
Sonata ASO
Ballad Plus

Formulation and application details

Usually supplied as a wettable powder or aqueous suspension that is applied as a foliar spray

Commercial production

Commercial production of Bacillus species typically involves large-scale aerobic fermentation. The process begins with selecting a robust strain, often genetically optimised for yield and stability. These bacteria are cultivated in bioreactors under tightly controlled conditions, temperature (usually 30–37 degrees C), pH (neutral to slightly alkaline), and oxygen levels are carefully regulated to maximise growth and productivity. Nutrient-rich media, often containing glucose or other carbon sources, support rapid biomass accumulation. After fermentation, the culture is harvested, and the desired products, such as enzymes or spores, are extracted and purified.

Impact on climate of production and use

As microbial-based biopesticide production processes tend to use fermentation-based production rather than chemical synthesis, have a lower fossil fuel input in formulation and active ingredient creation, and have reduced downstream emissions due to biodegradability and minimal soil disruption, the life-cycle GHG emissions are expected to be low. Whilst hard and precise data are not available, broad estimates suggest that typically emissions are likely to be below 5 kg CO₂e/kg.

ENVIRONMENTAL FATE

Property

Value

Source; quality score; and other information

Interpretation

Solubility - In water at 20 °C (mg l⁻¹)

Solubility - In organic solvents at 20 °C (mg l⁻¹)

Melting point (°C)

Boiling point (°C)

Degradation point (°C)

Flashpoint (°C)

Octanol-water partition coefficient at pH 7, 20 °C

Log P

Fat solubility of residues

Solubility

Data type

Density (g ml⁻¹)

Dissociation constant pKa) at 25 °C

Vapour pressure at 20 °C (mPa)

Henry's law constant at 25 °C (Pa m³ mol⁻¹)

Volatilisation as max % of applied dose lost

From plant surface

From soil surface

Maximum UV-vis absorption L mol⁻¹ cm⁻¹

Surface tension (mN m⁻¹)

Degradation

Property

Value

Source; quality score; and other information

Interpretation

General biodegradability

Soil degradation (days) (aerobic)

DT₅₀ (typical)

DT₅₀ (lab at 20 °C)

DT₅₀ (field)

DT₉₀ (lab at 20 °C)

DT₉₀ (field)

DT₅₀ modelling endpoint

Note

Dissipation rate RL₅₀ (days) on plant matrix

Value

Note

Dissipation rate RL₅₀ (days) on and in plant matrix

Value

Note

Aqueous photolysis DT₅₀ (days) at pH 7

Value

Note

Aqueous hydrolysis DT₅₀ (days) at 20 °C and pH 7

Value

Note

Water-sediment DT₅₀ (days)

Water phase only DT₅₀ (days)

Sediment phase only DT₅₀ (days)

Air degradation

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.

Decay in stored produce DT₅₀

Soil adsorption and mobility

Property

Value

Source; quality score; and other information

Interpretation

Linear

K_d (mL g⁻¹)

K_oc (mL g⁻¹)

Notes and range

Freundlich

K_f (mL g⁻¹)

K_foc (mL g⁻¹)

¹/_n

Notes and range

pH sensitivity

Known metabolites

None

ECOTOXICOLOGY

Terrestrial ecotoxicology

Property

Value

Source; quality score; and other information

Interpretation

Mammals - Acute oral LD₅₀ (mg kg⁻¹)

> 4.1 x 10⁰⁹

Rat as CFU animal⁻¹

Mammals - Short term dietary NOEL

(mg kg⁻¹)

(ppm diet)

Mammals - Chronic 21d NOAEL (mg kg⁻¹ bw d⁻¹)

Birds - Acute LD₅₀ (mg kg⁻¹)

> 7.0 x 10¹⁰

Unknown species as CFU/kg BW/day

Birds - Short term dietary (LC₅₀/LD₅₀)

Birds - Chronic 21d NOEL (mg kg⁻¹ bw d⁻¹)

Earthworms - Acute 14 day LC₅₀ (mg kg⁻¹)

> 2.1 x 10¹²

as CFU/kg dry soil

Earthworms - Chronic NOEC, reproduction (mg kg⁻¹)

Soil micro-organisms

Collembola

Acute LC₅₀ (mg kg⁻¹)

Chronic NOEC (mg kg⁻¹)

Non-target plants

Vegetative vigour ER₅₀ (g ha⁻¹)

Seedling emergence ER₅₀ (g ha⁻¹)

Honeybees (Apis spp.)

Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

Unknown mode acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

Non-toxic

No adverse effects identified or expected

Non-toxic

Chronic

Notes

Bumblebees (Bombus spp.)

Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

Mason bees (Osmia spp.)

Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

Other bee species (1)

Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)

Mode of exposure

Other bee species (2)

Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)

Mode of exposure

Beneficial insects (Ladybirds)

Beneficial insects (Lacewings)

Beneficial insects (Parasitic wasps) as Mortality LR₅₀ CFU/ha

3.5 x 10¹⁴

Aphidius rhopalosiphi

Low

Beneficial insects (Predatory mites) as Mortality LR₅₀ CFU/ha

3.5 x 10¹⁴

Typhlodromus pyri

Low

Beneficial insects (Ground beetles)

Aquatic ecotoxicology

Property

Value

Source; quality score; and other information

Interpretation

Temperate Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)

No adverse effects identified or expected

Temperate Freshwater Fish - Chronic 21 day NOEC (mg l⁻¹)

No adverse effects identified or expected

Tropical Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)

Temperate Freshwater Aquatic invertebrates - Acute 48 hour EC₅₀ (mg l⁻¹)

6.2 x 10⁰⁸

Daphnia magna as CFU/L 21 day

Temperate Freshwater Aquatic invertebrates - Chronic 21 day NOEC (mg l⁻¹)

Tropical Freshwater Aquatic invertebrates - Acute 48 hour EC₅₀ (mg l⁻¹)

Aquatic crustaceans - Acute 96 hour LC₅₀ (mg l⁻¹)

Sediment dwelling organisms - Acute 96 hour LC₅₀ (mg l⁻¹)

Sediment dwelling organisms - Chronic 28 day NOEC, static, water (mg l⁻¹)

Sediment dwelling organisms - Chronic 28 day NOEC, sediment (mg kg⁻¹)

Aquatic Plants (free-floating, fonds growth, fresh) - 7 day (mg l⁻¹) (EC₅₀)

> 1.2 x 10⁰⁹

Lemna gibba as CFU/L

Aquatic plants (rooted, growth rate, fresh) - 14 day (mg l⁻¹)

Algae - Acute (growth rate, fresh; mg l⁻¹)

Algae - Chronic (growth rate, fresh; mg l⁻¹)

No adverse effects identified or expected

Mesocosm study data

NOEAEC mg l⁻¹

Marine bivalves

HUMAN HEALTH AND PROTECTION

General

Property

Value

Source; quality score; and other information

Interpretation

Threshold of Toxicological Concern (Cramer Class)

Not applicable

Mammals - Acute oral LD₅₀ (mg kg⁻¹)

> 4.1 x 10⁰⁹

Rat as CFU animal⁻¹

Mammals - Dermal LD₅₀ (mg kg⁻¹ body weight)

1.6E+08

Rat as CFU animal⁻¹

Mammals - Inhalation LC₅₀ (mg l⁻¹)

> 1.6E+08

Rat as CFU animal⁻¹

Other Mammal toxicity endpoints

Intravenous LD₅₀ > 7.1E+08 CFU kg⁻¹ BW

ADI - Acceptable Daily Intake (mg kg⁻¹ bw day⁻¹)

None allocated

ARfD - Acute Reference Dose (mg kg⁻¹ bw day⁻¹)

None allocated

AAOEL - Acute Acceptable Operator Exposure Level (mg kg⁻¹ bw day⁻¹)

AOEL - Acceptable Operator Exposure Level - Systemic (mg kg⁻¹ bw day⁻¹)

None allocated

Dermal penetration studies (%)

Dangerous Substances Directive 76/464

Exposure Routes

Public

No risk expected

Occupational

No risk expected

Mammalian dose elimination route and rate

Health issues

Specific human health issues

Carcinogen

Genotoxic

Endocrine disruptor

; ; ; ;

Reproduction / development effects

Acetyl cholinesterase inhibitor

Neurotoxicant

Respiratory tract irritant

Skin irritant

Skin sensitiser

Eye irritant

Phototoxicant

No data found

General human health issues

Not expected to be harmful to humans

Handling issues

Property

Value and interpretation

General

Incompatible with strong oxidants, acids and alkais

CLP classification 2013

WHO Classification

Not listed (Not listed)

UN Number

Waste disposal & packaging

Shelf-life, storage, stability and reactivity

TRANSLATIONS

Language

Name

English

Bacillus pumilus strain QST 2808

French

Bacillus pumilus

German

Bacillus pumilus

Danish

Bacillus pumilus

Italian

Bacillus pumilus

Spanish

Bacillus pumilus

Greek

Bacillus pumilus

Polish

Bacillus pumilus

Swedish

Bacillus pumilus

Hungarian

Bacillus pumilus

Dutch

Bacillus pumilus

Norwegian

Record last updated:	25/08/2025
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