| Emamectin B1a |

Last updated: 13/02/2026
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(Also known as: abamectin-aminomethyl B1a) |
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 naturally occuring soil Actinomycete effective against various insect pests |
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Caterpillars; Mites; Thrips; Leaf miners |
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Fruit trees; Leafy crops including lettuce, brassicas |
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- |
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- |
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- |
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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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Approved |
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Netherlands |
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15/11/2026 |
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Yes - low ADI/ARfD/AOEL |
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Yes |
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ATAustria |
BEBelgium |
BGBulgaria |
CYCyprus |
CZCzech Republic |
DEGermany |
DKDenmark |
EEEstonia |
ELGreece |
| ✓ |
✓ |
✓ |
✓ |
  |
  |
  |
  |
✓ |
ESSpain |
FIFinland |
FRFrance |
HRCroatia |
HUHungary |
IEIreland |
ITItaly |
LTLithuania |
LULuxembourg |
| ✓ |
  |
✓ |
✓ |
✓ |
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✓ |
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  |
LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
|   |
  |
✓ |
✓ |
✓ |
✓ |
  |
✓ |
✓ |
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ISIceland |
NONorway |
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Emamectin B1a exhibits complex stereoisomerism due to its large, polycyclic structure and numerous chiral centres. The molecule contains multiple asymmetric carbon atoms, each capable of adopting either R or S configuration, which gives rise to a specific three-dimensional arrangement essential for its biological activity. Emamectin B1a also includes conjugated double bonds, which introduce geometric (E/Z) isomerism. The biologically active form used in veterinary medicine is a single stereoisomer, carefully controlled during synthesis to maintain efficacy and safety. |
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C₄₉H₇₅NO₁₃ |
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CCC(C)C1C(C=CC2(O1)CC3CC(O2)CC=C(C(C(C=CC=C4COC5C4(C(C=C(C5O)C)C(=O)O3)O)C)OC6CC(C(C(O6)C)OC7CC(C(C(O7)C)NC)OC)OC)C)C |
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CC[C@H](C)[C@@H]1[C@H](C=C[C@@]2(O1)C[C@@H]3C[C@H](O2)C/C=C(/[C@H]([C@H](/C=C/C=C/4\CO[C@H]5[C@@]4([C@@H](C=C([C@H]5O)C)C(=O)O3)O)C)O[C@H]6C[C@@H]([C@H]([C@@H](O6)C)O[C@H]7C[C@@H]([C@@H]([C@@H](O7)C)NC)OC)OC)\C)C |
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CXEGAUYXQAKHKJ-COFQVFHOSA-N |
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InChI=1S/C49H75NO13/c1-12-26(2)44-29(5)18-19-48(63-44)24-35-21-34(62-48)17-16-28(4)43(27(3)14-13-15-33-25-56-46-42(51)30(6)20-36(47(52)59-35)49(33,46)53)60-40-23-38(55-11)45(32(8)58-40)61-39-22-37(54-10)41(50-9)31(7)57-39/h13-16,18-20,26-27,29,31-32,34-46,50-51,53H,12,17,21-25H2,1-11H3/b14-13+,28-16+,33-15+/t26-,27-,29-,31-,32-,34+,35-,36-,37-,38-,39-,40-,41+,42+,43-,44+,45-,46+,48+,49+/m0/s1 |
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Yes |
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Fungicide; Other substance; Veterinary substance |
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Bactericide |
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Micro-organism derived substance |
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- |
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- |
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Natural |
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Non-systemic, acts by causing insect paralysis. Glutamate-gated chloride channel (GluCl) allosteric modulator. |
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Produced by the fermentation of the soil actinomycete Streptomyces avermitilis |
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Crop protection |
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Caterpillars; Mites; Thrips; Leaf miners |
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Fruit trees; Leafy crops including lettuce, brassicas |
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- |
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121124-29-6 |
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- |
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791 |
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- |
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- |
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886.1 |
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- |
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(10E,14E,16E)-(1R,4S,5S,6S,6R,8R,12S,13S,20R,21R,24S)-6-[(S)-secbutyl]-21,24-dihydroxy-5,11,13,22-tetramethyl-2-oxo-(3,7,19-trioxatetracyclo[15.6.1.1.0]pentacosa-10,14,16,22-tetraene)-6-spiro-2Œ-(5,6-dihydro-2H-pyran)-12-yl 2,6-dideoxy-3-O-methyl-4-O-(2,4,6-trideoxy-3-O-methyl-4-methylamino-α-L-lyxo-hexapyranosyl)-)α-L-arabino-hexapyranoside |
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(4R)-5-O-demethyl-4-deoxy-4-(methylamino)avermectin A1a |
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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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Yes [ R12 Rule 12: Pesticide active ingredients that are bioaccumulative (where bio-concentration factor (BCF) > 2000 l kg⁻¹ (if BCF is not available, where Log P >=5)) ] |
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- |
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Not applicable |
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Not applicable |
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6 |
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BM02 |
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- |
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White or faintly yellow powder |
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Current |
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1997, introduced Israel and Japan; 1999, introduced USA |
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- Syngenta AG
- MSD Animal Health UK Ltd
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- Tree-age
- Proclaim
- Affirm
- Denim
- Rivaive
- Slice 2 Premix
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Usually formulated as the benzoate. It is usually supplied as an emulsifiable concentrate and soluble granules for crops & as a trunk injection for trees. Often used as medicated pre-mix feed for animal health. |
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Emamectin B1a is produced commercially through a multi-step chemical synthesis process. The process begins with the fermentation of a specific strain of the bacterium Streptomyces avermitilis, which produces avermectin B1a as a secondary metabolite. The avermectin B1a is then chemically modified to produce emamectin B1a. This involves several steps, including oxidation and amination reactions. The resulting emamectin B1a is purified to remove any impurities and by-products. This is typically done using high-performance liquid chromatography (HPLC) or other purification techniques. |
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There is no publicly available LCA data on GHG emissions specifically for the manufacture of emamectin B1a. However, based on similar fermentation-derived fungicides and estimated GHG emissions: are in the region of 10–25 kg CO₂e per kg of emamectin B1a |
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21 |
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Moderate |
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1.00 X 1005 |
Calculated |
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5.0 |
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High |
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Soluble |
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Regulatory data - observed in metabolism and farm animal feeding studies |
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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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Major fraction |
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Major fraction |
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Major fraction |
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Major fraction |
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| Known groundwater metabolites |
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None
None
| Terrestrial ecotoxicology |
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89.0 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Rat |
High |
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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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8.9 |
Worst case of acute and chronic mammals |
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No data |
No data for 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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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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No data |
No data for temperate acute and chronic fish |
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No data |
No data for temperate acute and chronic aquatic invertebrates |
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No data |
No data for free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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High (class III) |
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89.0 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Rat |
High |
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Partially metabolised and excreted mainly in the faeces |
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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 |
No data found |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
?Possibly, status not identified |
XNo, known not to cause a problem |
?Possibly, status not identified |
| Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
| No data found |
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 climical tremors |
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Not explosive or oxidising Not explected to auto-ignite, Not highly flammable |
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Health: H301, H311, H331, H372, H318, H319 Environment: H400 |
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II (Moderately hazardous) |
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emamectin B1a |
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| 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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