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Sugarbeet root extract
Last updated: 13/02/2026
(Not known by any other names)

GENERAL INFORMATION
Description
A botanical extract intended for use as a natural elicitor to enhance plant defences against fungal infections
Examples of veterinary uses
-
Examples of species treated
-
Approval status
VMR 2013/2033 approval status (GB/UK)
-
EU Regulatory approval status
-
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?
No
General status
Veterinary substance type
-
Other bioactivity & uses
Biostimulant - improved disease resiliance, growth enhancement and quality traits; Plant elicitor
Substance groups
Plant derived substance
Minimum active substance purity
-
Known relevant impurities
Contaminants potentially arising from production and formulation (e.g. endotoxins and chemical residues) may mediate Horizontal Gene Transfer or allergic reactions - purity is important
Substance origin
Natural; Complex mixture
Mode of action
Not direct fungicidal activity but acts through indirect modes of action including as an osmo-protectant & resistance inducer which up-regulates the plants own defences against fungal infections.
Molecular targets
-
CAS RN
89957-89-1
EC number
-
CIPAC number
-
US EPA chemical code
-
PubChem CID
-
Therapeutic Class
-
ATCvet Code
-
Controlled Drug?
-
Regulation 37/2010 MRL Classification
-
Molecular mass
-
Chemical name
Sugarbeet root extract
PIN (Preferred Identification Name)
-
IUPAC name
-
CAS name
-
Global Governance status: Listed (✓) under
UK Poisons List Order 1972 Rotterdam Convention Montreal Protocol
Stockholm Convention OSPAR EU Water Framework Directive
Relevant Environmental Water Quality Standards
-
Forever chemical
-
Other status information
-
Physical state
Dark brown viscous liquid
Related substances & organisms
Commercial
Property
Value
Availability status
Current
Introduction & key dates
2026, first registered Australia
Example manufacturers & suppliers of products using this active now or historically
  • Adama Australia Pty Ltd
Example products using this active
  • Actavan Bio Plant Defence Elicitor
  • Actavan
Formulation and application details
Available as a soluble concentrate and applied as a dilute aqueous spray; a non-ionic adjuvant is recommended
Commercial production
Sugar beet leaf extract is produced by first harvesting the leaves during sugar beet root collection, followed by cleaning, washing to remove soil, and drying, most commonly freeze-drying to preserve nutrients, though oven-drying or air-drying may be used. The dried leaves are then ground into a fine powder, often with liquid nitrogen for better cell disruption. Extraction employs various methods, including conventional solvent maceration (e.g., with 50-70% methanol or ethanol, often acidified with formic acid), ultrasound-assisted extraction, microwave-assisted extraction, pressurised liquid extraction, or subcritical water extraction. The mixture is filtered or centrifuged to separate the liquid extract, which may undergo concentration (e.g., evaporation) and further drying (often freeze-drying) to yield a powdered or concentrated form.
Impact on climate of production and use
Data for the GHG emissions from the production of sugarbeet root extract are not available in open literature. Emissions will vary significantly based on factors like cultivation practices, extraction method (water-based is lower-impact than solvent-based), energy sources (fossil vs. renewable), and whether the extract is a dedicated product or byproduct (affecting allocation of emissions). Based on sugarbeet LCAs and bio-stimulant analogs, rough estimates can be determined. For efficient process (e.g. byproduct-based with renewable energy extraction) emissions can be expected to be low at around 0.5-2 kg CO₂e per kg concentrated extract (cradle-to-gate). Mid-range efficiency process (e.g. typical water diffusion and using fossil energy): emissions would be expected to be 1.0-5.0 kg CO₂e per kg. However, for extract production based on dedicated cultivation and energy-intensive concentration steps emissions would be higher and typically in the range: 3-10 kg CO₂e per kg.
ENVIRONMENTAL FATE
Property
Value
Source; quality score; and other information
Interpretation
Solubility - In water at 20 °C at pH 7 (mg l⁻¹)
- - -
Solubility - In organic solvents at 20 °C (mg l⁻¹)
10000
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Toluene
-
10000
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Methanol
-
10000
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Dichloromethane
-
10000
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Ethyl acetate
-
Melting point (°C)
- - -
Boiling point (°C)
100
P3 P = Other non-EU, UK or US Governments and Regulators
3 = Unverified data of known source
-
Degradation point (°C)
- - -
Flashpoint (°C)
- - -
Octanol-water partition coefficient at pH 7, 20 °C
P
- - -
Log P
- - -
Fat solubility of residues
Solubility
- - -
Data type
- - -
Density (g ml⁻¹)
1.179
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
-
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
pH 1.5: 265nm = 4931
pH 6.8: 263nm = 4097
pH 12.0: 265nm=5717
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
-
Surface tension (mN m⁻¹)
- - -
Refractive Index
- - -
Environmental release
-
Degradation
Property
Value
Source; quality score; and other information
Interpretation
Soil degradation (days) (aerobic)
DT₅₀ (typical)
- - -
DT₅₀ (lab at 20 °C)
- - -
DT₅₀ (field)
- - -
DT₉₀ (lab at 20 °C)
- - -
DT₉₀ (field)
- - -
Note
-
Manure DT₅₀ (days)
- - -
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)
1.0
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Moderately fast
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
Kd (mL g⁻¹)
- - -
Koc (mL g⁻¹)
-
Notes and range
-
Freundlich
Kf (mL g⁻¹)
- - -
Kfoc (mL g⁻¹)
-
1/n
-
Notes and range
-
pH sensitivity
-
Fate indices
Property
Value
Source; quality score; and other information
Interpretation
GUS leaching potential index
- - -
Bio-concentration factor
BCF (l kg⁻¹)
- - -
CT₅₀ (days)
- -
Known metabolites

None

ECOTOXICOLOGY
Terrestrial ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Mammals - Acute oral LD₅₀ (mg kg⁻¹)
- - -
Mammals - Short Term Oral NOAEL (mg kg⁻¹ bw d⁻¹)
- - -
Mammals - Long Term (Chronic) Oral NOAEL (mg kg⁻¹ bw d⁻¹)
> 1560
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Rat as trimethylglycine
Low
Birds - Acute LD₅₀ (mg kg⁻¹)
> 2000
P3 P = Other non-EU, UK or US Governments and Regulators
3 = Unverified data of known source
Unknown species as trimethylglycine
Low
Birds - Short term dietary LC₅₀ (mg kg⁻¹ bw d⁻¹)
- - -
Birds - Chronic 21d NOEL (mg kg⁻¹ bw d⁻¹)
- - -
Earthworms - Acute 14 day LC₅₀ (mg kg⁻¹ dw soil)
- - -
Earthworms - Chronic NOEC, reproduction (mg kg⁻¹ dw soil)
> 338
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Eisenia foetida as EC10
Low
Soil micro-organisms
Nitrogen transformation: No significant effect
P5 P = Other non-EU, UK or US Governments and Regulators
5 = Verified data used for regulatory purposes
-
Collembola
Acute LC₅₀ (mg kg⁻¹)
- - -
Chronic NOEC (mg kg⁻¹)
780
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Folsomia candida
-
Non-target plants
Vegetative vigour ER₅₀ (g ha⁻¹)
> 17900
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Avena sativa as trimethylglycine
-
Seedling emergence ER₅₀ (g ha⁻¹)
> 17900
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Avena sativa as trimethylglycine
-
Honeybees (Apis spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
> 527
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Apis mellifera as trimethylglycine
Low
Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
> 527
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Apis mellifera as trimethylglycine
Low
Unknown mode acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
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 LR₅₀ g ha⁻¹
> 10800
P5 P = Other non-EU, UK or US Governments and Regulators
5 = Verified data used for regulatory purposes
Aphidius rhopalosiphi
Low
Beneficial insects (Predatory mites) as LR₅₀ g ha⁻¹
> 10800
P5 P = Other non-EU, UK or US Governments and Regulators
5 = Verified data used for regulatory purposes
Typhlodromus pyri)
Low
Beneficial insects (Ground beetles)
- - -
Beneficial insects (Butterflies)
Contact
- - -
Notes
-
Oral
- - -
Notes
-
Aquatic ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Temperate Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)
> 78.0
P5 P = Other non-EU, UK or US Governments and Regulators
5 = Verified data used for regulatory purposes
Oncorhynchus mykiss
Moderate
Temperate Freshwater Fish - Chronic 21 day NOEC (mg l⁻¹)
- - -
Tropical Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)
- - -
Temperate Freshwater Aquatic invertebrates - Acute 48 hour EC₅₀ (mg l⁻¹)
- - -
Temperate Freshwater Aquatic invertebrates - Chronic 21 day NOEC (mg l⁻¹)
> 100
P5 P = Other non-EU, UK or US Governments and Regulators
5 = Verified data used for regulatory purposes
Daphnia magna
Low
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)
- - -
Aquatic plants (rooted, growth rate, fresh) - 14 day (mg l⁻¹)
- - -
Algae - Acute (growth rate, fresh; mg l⁻¹) (P5 Pseudokirchneriella subcapitata)
> 100 - Low
Algae - Chronic (growth rate, fresh; mg l⁻¹)
- - -
Mesocosm study data
NOEAEC mg l⁻¹
- - -
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)
- - -
Mammals - Acute oral LD₅₀ (mg kg⁻¹)
- - -
Mammals - Short Term Oral NOAEL (mg kg⁻¹ bw d⁻¹)
- - -
Mammals - Long Term (Chronic) Oral NOAEL (mg kg⁻¹ bw d⁻¹)
> 1560
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
Rat as trimethylglycine
Low
Mammals - Dermal LD₅₀ (mg kg⁻¹ body weight)
- - -
Mammals - Inhalation LC₅₀ (mg l⁻¹)
- - -
Other Mammal toxicity endpoints
- - -
ADI - Acceptable Daily Intake (mg kg⁻¹ bw day⁻¹)
None allocated
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
-
ARfD - Acute Reference Dose (mg kg⁻¹ bw day⁻¹)
None allocated
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
-
AAOEL - Acute Acceptable Operator Exposure Level (mg kg⁻¹ bw day⁻¹)
None allocated
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
-
AOEL - Acceptable Operator Exposure Level - Systemic (mg kg⁻¹ bw day⁻¹)
None allocated
P4 P = Other non-EU, UK or US Governments and Regulators
4 = Verified data
-
Dermal penetration studies (%)
- - -
Dangerous Substances Directive 76/464
- - -
Exposure Routes
Public
Negligible risks
Occupational
Negligible risks
Mammalian dose elimination route and rate
- - -
Health issues
Specific human health issues (hazard-based)
Carcinogen
Genotoxic
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
;
E0 E = Unspecified genotoxicity type (miscellaneous data source)
0 = No data
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
XNo, known not to cause a problem
XNo, known not to cause a problem
XNo, known not to cause a problem
Eye irritant Phototoxicant  
XNo, known not to cause a problem
No data found  
General human health issues
No information available
Handling issues
Property
Value and interpretation
General
TMG is hydrophilic
Not expected to auto-ignite; Not highly flammable
CLP classification 2013
-
WHO Classification
-
UN Number
Not regulated
Waste disposal & packaging
-
Shelf-life, storage, stability and reactivity
Stable when stored at temps up to 54 °C for at least 2 weeks
TRANSLATIONS
Language
Name
English
sugarbeet root extract
French
-
German
-
Danish
-
Italian
-
Spanish
-
Greek
-
Polish
-
Swedish
-
Hungarian
-
Dutch
-
Norwegian
-

Record last updated: 13/02/2026
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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