- Aquatic Ecotoxicology
- OECD 202: Daphnia sp., Acute Immobilisation Test
- OECD 211: Daphnia magna Reproduction Test
- OECD 235: Chironomus sp., Acute Immobilisation Test
- OECD 218/219: Sediment-Water Chironomid Toxicity Test Using Spiked Sediment/Spiked Water
- OECD 233: Sediment-Water Chironomid Life-Cycle Toxicity Test Using Spiked Water or Spiked Sediment
- OECD 225: Sediment-water Lumbriculus Toxicity Test Using Spiked Sediment
- OECD 242: Potamopyrgus antipodarum Reproduction Test
- OECD 243: Lymnaea stagnalis Reproduction Test
- OECD 203: Fish, Acute Toxicity Test
- OECD 215: Fish Juvenile Growth Study
- OECD 212: Fish, Short-term Toxicity Test on Embryo and Sac-fry Stages
- OECD 231: The Amphibian Metamorphosis Assay
- OECD 236: Fish Embryo Acute Toxicity Test
- OECD 210: Fish, Early-life Stage Toxicity Test
- OECD 229 Fish Short Term Reproduction Assay and OECD 230 21-day Fish Assay
- OECD 240 Medaka Extended One Generation Reproduction Test (MEOGRT)
- OECD 248: Xenopus Eleutheroembryonic Thyroid Assay
- OPPTS 850.1500: Fish Life Cycle Toxicity Test
- OÈCD 234 Fish sexual development test
- Storage Stability Studies
- OPPTS 830.6302, OPPTS 830.6303,and OPPTS 830.6304: Physical State, Colour and Odor at 20 °C and at 101.3 kPa
- EU A.1: Melting temperature/range
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- EU A.3: Relative density (liquids and solids)
- EU A.4: Vapour pressure
- EU A.5: Surface tension
- EU A.9: Flashpoint
- EU A.10: Flammability (solids)
- EU A.12: Flammability (contact with water)
- EU A.13: Pyrophoric properties of solids and liquids
- EU A.16: Relative self-ignition temperature for solids
- EU A.17: Oxidising properties
- OECD 114: Viscosity of Liquids
- Environmental Fate
- Terrestrial Ecotoxicology
- Non-target arthropod testing with the parasitic wasp (Aphidius rhopalosiphi)
- Non-target arthropod testing with the lacewing (Chrysoperla carnea)
- Non-target arthropod testing with the ladybird beetle (Coccinella septempunctata)
- Non-target arthropod testing with the predatory bug (Orius laevigatus)
- Non-target arthropod testing with the predatory mite (Typhlodromus pyri)
- Non-target arthropod testing with the rove beetle (Aleochara bilineata)
- Non-target arthropod testing with the carabid beetle (Poecilus cupreus)
- Non-target arthropod testing with the wolf spider (Pardosa spec.)
- OECD 213/214: Honey bees, Acute Oral and Acute Contact Toxicity Test
- OECD 245: Honey Bee (Apis Mellifera L.), Chronic Oral Toxicity Test (10-Day Feeding)
- OECD 237: Honey Bee Larval Toxicity Test, Single Exposure
- OECD 239: Honey Bee Larval Toxicity Test
- EPPO 170: Honey Bee Field Study – do plant protection products effect honey bee colonies?
- Oomen et al. 1992: Honey Bee Brood Feeding Study
- OECD 75: Honey Bee Brood Test under Semi-field Conditions in Tunnels
- OECD 246/247 Acute Oral and Contact Toxicity to the Bumblebee, Bombus terrestris L.
- Solitary Bee Acute Contact Toxicity Study in the Laboratory (Osmia sp.) Solitary Bee Acute Oral Toxicity Study in the Laboratory (Osmia sp.) (protocols for ringtests with solitary bees recommended by the non-Apis working group)
- SANTE/11956/2016 rev.9 Residue trials for MRL setting in honey
- OECD 208: Terrestrial Plant Test - Seedling Emergence and Seedling Growth Test
- OECD 227: Terrestrial Plant Test - Vegetative Vigour Test
- OCSPP 850.4100: Seedling Emergence and Seedling Growth
- OCSPP 850.4150: Vegetative Vigor
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Earthworm Field Study (ISO 11268-3)
Advanced risk assessment on earthworm populations in natural environment
Environmental risk assessments of plant protection products and in specific cases also of veterinary medicinal products take into account the effects of substances on soil organisms like e.g. earthworm species. If prior laboratory studies are not sufficient to exclude unacceptable effects on earthworms it may be necessary to start with a higher tier approach by performing earthworm field studies under realistic conditions as given by GAP (good agricultural practice) to receive further data for the decision makers.
according to ISO 11268-3
Earthworms, living in natural populations. Adults are identified to species level, juveniles are assigned to the two morphological groups: tanylobous and epilobous.
Design of the Test Field
The basic study design comprises three treatment groups: the test item treatment, the water treated control and the toxic reference item treated with 6 to 10 kg/ha carbendazim. Each treatment has four replicates (plots) arranged in a randomized plot design (plot size 10 m x 10m). Distance between the plots is at least 3 m and approximately 10 m distance to the fields next to the test site. Sampling plots are chosen from grassland or arable field sites with homogeneous conditions.
Application of Test Substances
The application of the test substances are carried out with a calibrated movable plot sprayer or granule applicator. The number of test item applications and application rates follows the principles of GAP taking into account realistic conditions of application, product persistence and possible interception by vegetation.
Analytical Verification of the Test Item Application
According to ISO 11268-3 the application of the test item has to be analytically verified. ibacon offers three methods for verfication:
- analysis of spray liquid samples taken before test item application
- determination of the a.i. content in soil samples
- analysis of spray residues from Petri dishes placed on the test item treated plots during application
Formaldehyde extraction combined with hand sorting.
In a first step the upper soil layer (circa 0-20 cm) of a sample place (size 0.125 to 1.0 m²) is excavated and the soil and vegetation layer are carefully searched for earthworms. For the investigation of deeper soil layers 5 to 10 liters of an aqueous solution of 0,2% formaldehyde is uniformly applied to the remaining surfaces of the trial plots. After a few minutes the earthworms come to the soil surface and are collected into a preservation liquid. Four samples are taken per plot (= 16 per treatment group).
Recording of environmental Conditions
Soil parameter and climate data are taken throughout the study.
Soil characterisation: soil profile, pH, C-content, water holding capacity, particle size composition, vegetation observation
Microclimate: soil and air temperature, soil humidity, precipitation
Course of the Study
Prior to the test item application a pre-sampling on the testing site verifies the required earthworm abundance and presence of important ecological groups (anecic and endogeic species). After test item application artificial overhead irrigation can be necessary to ensure exposure of earthworms if insufficient rainfall (under 10 mm) occurs within three days after application. Three additional earthworm samplings are performed within the next 12 months after the test item application.
Sampling dates: pre-application sampling within 14 days before application, three post application samplings approx. 1, 4-6 and 12 months after last test item application
Duration: 1 year
Abundance and biomass of adult and juvenile earthworms are monitored over a time period of one year. The data of the most abundant species are analysed in detail. The results are evaluated for possible differences of the control compared with the test and reference item treatment.
Guidelines and Literature
ISO 11268-3 / 2014/ Soil quality - Effects of pollutants on earthworms - Part 3: Guidance on the determination of effects in field situations", 2nd edition.
Kula et al. 2006: Technical recommend-dations for the update of the ISO Earthworm Field Test Guideline (ISO-11268-3). Journal of Soils and Sediments 6: 182-186.
ISO 23611-1 / 2006 / Soil quality – sampling of soil invertebrates – Part 1: Hand-sorting and formalin extraction of earthworms.