| Sea algae extract |

Last updated: 18/02/2026
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(Also known as: Marine algae extracts; Seaweed extract) |
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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Aqueous extracts of various species of seaweed (e.g. Sargassum) that can be used as a plant growth regulator and biostimulant for various horticultural crops |
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Growth; Vigour; Stress |
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Legumes; Carrots |
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Sea algae extracts have been extensively studied as biostimulants and a significant body of evidence exists demonstrating improved plant growth, nutrition, quality, yield and stress tolerance (drought, salt conditions). Generally, overall plant perfomance improves following application including increased root growth & mineral uptake, as well as enhanced chlorophyll content. Various different seaweed extracts have been used in product formulations with brown algae the most commonly used. However, efficacy has been shown to be dependant on various factors including the source of seaweed, the extraction method utilised, how it is stored and formulated. |
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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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Belgium/Italy |
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Not applicable |
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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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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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Other substance |
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Biostimulant - improved abiotic stress resiliance; growth enhancement & improved nutrient use efficiency |
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Plant-derived substance; Marine algae-based biostimulant |
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EU dossier - none declared |
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Natural; Complex mixture |
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Biostimulant mechanisms are not fully understood with various potential pathways identified. A phytoelicitor activity appears to improve defence responses in plants that contribute to the various biostimulant effects. Other research suggests that the beneficial effects appear to be largely a function of other biomolecules (carbohydrates, polyphenols, etc.), which modulate gene expression and induce metabolic changes in plants. |
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Extracts from one or more of the following species: Ascophyllium nodosum, Lammaria spp., Macrocystis integrifolia, Fucales spp. and others |
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Sea algae extracts contain a diverse array of primary and secondary metabolites, varying by species, harvest conditions, season, and extraction method. The major fraction is comprised of polysaccharides (20-50%) and these include alginic acid/alginates (20-30% in brown algae), fucoidans (5-15%), laminarin (beta-glucan reserve polysaccharide), ulvans (in green algae), carrageenans (in red algae). Proteins/peptides and amino acids are also a significant component with variable concentrations at around 10–20%. Minerals and trace elements can also be a major component (5-25%). Phenolic compounds/polyphenols can account for 10% or more and these substances include phlorotannins (unique to brown algae), flavonoids, bromophenols, phenolic acids. Mannitol (an osmoprotectant) can be present at 5–10% in some brown species. Sea algae extracts will also contain small amounts of plant growth regulators and hormones such as auxins, cytokinins, gibberellins, betaines, polyamines as well as lipids and fatty acids. In terms of its bioactivity, no single compound dominates, as efficacy arises from synergistic interactions among the mixture. However, key contributors to biopesticide activity include sulphated polysaccharides, alginic acid/alginates and phlorotannins and other polyphenols. |
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Crop protection; Yield enhancement; Biostimulant |
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Legumes; Carrots |
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Suitable for use in all farming systems where approved for use in that country |
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Sea algae extracts |
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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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Not applicable |
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Green-brown coloured liquid |
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Current |
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Circa 1950, introduced |
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- Bionema Group
- Biolchim SA, Italy
- Goemar Le Laboratoire de la mar S.A
- Asfeleia srl
- Oilean Glas Teoranta
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- Groprim
- Actiwave
- Althia
- Kelpgrow
- AlgaeGreen 500
- NueCombi
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Usually supplied as an aqueous solution and applied as a spray |
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The exact process used to produce the extract will vary depending on the Sea algae species. Generally, the seaweed is harvested, dried and ground into a powder. The valuable bioactive components are then extracted using various techniques including solvent extract, heat, microwave technologies or hydrolysis. The resulting material is then purified and formulated. |
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While precise life cycle assessments are still emerging, early analyses suggest that seaweed- and algae-based biostimulants may emit less than 1 kg CO₂e per kg of product, depending on the production system. |
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1.07 |
range 1.03-1.11 |
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47 |
range 23.1 - 70.5 |
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Readily biodegradable |
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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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> 2000 |
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Low |
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No adverse effects identified or expected |
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> 1000 |
Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source Expert judgement |
Low |
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> 100 |
Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source Expert judgement |
Low |
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100 |
Oncorhynchus mykiss as NOEC |
Moderate |
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100 |
Daphnia magna as product NOEC |
Moderate |
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> 100 |
Raphidocelis subcapitata |
Low |
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| Regulatory Threshold Levels (RTLs) used to calculate Total Applied Toxicity (TAT) |
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200 |
Worst case of acute and chronic mammals |
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No data |
No data for acute and chronic birds |
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200 |
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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No data |
No data for contact and oral honeybees |
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No data |
No data for parasitic wasps and predatory mites |
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1 |
Worst case of temperate acute and chronic fish |
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1 |
Worst case of temperate acute and chronic aquatic invertebrates |
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10 |
Worst case of free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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> 2000 |
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Low |
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> 2000 |
Rat |
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None allocated |
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None allocated |
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None allocated |
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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 |
No data found |
| Eye irritant |
Phototoxicant |
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?Possibly, status not identified |
No data found |
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No serious adverse health effects noted May cause gastrointestinal problems |
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IMDG Transport Hazard Class 3 |
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Not listed (Not listed) |
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UN1197 |
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Sea algae extract |
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| Record last updated: |
18/02/2026 |
| 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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