(Also known as: Pearly green lacewing; Aphid lion; Chrysopa carnea; Green lacewing; Predatory lacewing)
Hazard alerts
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
Human health Low alert
GENERAL INFORMATION
Description
A predatory insect valued for its role in biological pest control, feeding on aphids, whiteflies, and other soft-bodied pests
Example pests/issues controlled
Aphids; Mealybugs; Whiteflies; Scale; Thrips; Small caterpillars
Example applications
Soft fruit; Top fruit; Hops; Ornamentals; Greenhouse crops
Efficacy & activity
-
Appearance and life cycle
Adults are typically bright green with golden eyes and long, delicate, transparent wings featuring a fine network of veins. They are morphologically similar to Chrysoperla carnea but can be distinguished by subtle differences in genitalia and courtship songs
Example products using this substance as a possible coformulant
-
Formulation and application details
-
Commercial production
The commercial production of Chrysoperla lucasina relies on controlled conditions inside insectaries. Non-predatory adult lacewings are housed in large, specialised cages under controlled temperature, light, and humidity conditions where they are fed a semi-artificial, nutrient-rich liquid diet of honey, yeast, and sugar to maximise egg production. The stalked eggs are collected daily, often using mechanical harvesting methods or specialised substrates. Once the eggs are ready to hatch, the voracious, predatory larvae are immediately separated into individual containers to prevent them from eating one another. During this phase, they are reared on a cost-effective mass-produced host diet, most commonly the eggs of the Mediterranean flour moth or the rice moth. The insects are then packaged and shipped to agricultural facilities either as protected eggs or as active second-instar larvae mixed with an inert carrier material like buckwheat hulls, ready for rapid release to target aphids, thrips, and other soft-bodied crop pests.
Impact on climate of production and use
According to environmental studies, insect farming can produce as little as 1–5 kg CO₂e per kg of insect biomass, depending on species, feed type, and energy sources used
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)
-
-
-
Melting point (°C)
-
-
-
Boiling point (°C)
-
-
-
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)
-
-
-
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)
DT₅₀ (typical)
-
-
-
DT₅₀ (lab at 20 °C)
-
-
-
DT₅₀ (field)
-
-
-
DT₉₀ (lab at 20 °C)
-
-
-
DT₉₀ (field)
-
-
-
DT₅₀ modelling endpoint
-
-
-
Note
-
Soil mineralisation
Aerobic (at 20 °C)
-
-
-
Anaerobic (at 20 °C)
-
-
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
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
-
Known metabolites
None
ECOTOXICOLOGY
Terrestrial ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Mammals - Acute oral LD₅₀ (mg kg⁻¹)
-
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source
No adverse effects identified or expected
-
Mammals - Short Term Oral NOAEL (mg kg⁻¹ bw d⁻¹)
-
-
-
Mammals - Long Term (Chronic) Oral NOAEL (mg kg⁻¹ bw d⁻¹)
-
-
-
Birds - Acute LD₅₀ (mg kg⁻¹)
-
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source
Tzilivakis, J., Lewis, K.A., Green, A. and Warner, D.J. (2026) A decade of growth and impact of the Pesticide Properties Database (PPDB). Human and Ecological Risk Assessment: An International Journal, 1–26. DOI: 10.1080/10807039.2026.2702066
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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Human health
