Abstract
Purpose
Acute whole-sediment bioassay with the estuarine and marine amphipod Corophium volutator (Pallas) is widely used to assess toxicity of sediments. According to the guidelines DIN EN ISO 16712, mortality is the determined toxic endpoint. Additionally, the reburrowing ability of the surviving organisms of this acute toxicity test in fresh uncontaminated sediment is suggested as the sublethal endpoint, but insufficient information (e.g., exact measurement protocols) on this endpoint is provided, thus confounding factors and the interpretation of the results. The aim of this study was to provide information on burrowing activity as a sublethal endpoint.
Materials and methods
Amphipod tests were carried out in the laboratory, and the burrowing behavior was examined in a size- and gender-specific manner. For sediment testing, only animals of the same size were used in a defined sex ratio because it was found that female animals buried themselves faster than males and that smaller animals burrowed faster than bigger organisms. Statistical analyses were applied to determine whether burrowing time and ability differ significantly between sexes and sizes. Finally, tests were run to discern whether the burrowing ability could be a more sensitive endpoint than mortality.
Results and discussion
When the burrowing ability was examined in toxicity tests with contaminated sediment, the test organisms were affected in a dose-dependent manner. With rising concentrations of the contaminated sediment in a sublethal testing following the sediment exposure over 10 days, fewer animals buried themselves into the sediment.
Conclusions
The burrowing behavior can be used as an additional endpoint. For the tested sediment, burrowing was found to be more sensitive than the mortality. Guidance on the measurement protocol for this additional endpoint was developed. Under the test conditions examined, burrowing ability is an appropriate sublethal endpoint to supplement the toxicity test procedure.
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Notes
The sample was obtained from the sediment surface with a Van Veen grab sampler in 2006. An analysis of the chemical load was performed by the Gesellschaft für Bioanalytik Hamburg mbH, Hamburg (dry weight acc. DIN ISO 11465: 33.9 % w/w; particle size distribution acc. DIN 18123 per weight dry mass: <20 μm 55 %, 20–60 μm 14 %, 60–200 μm 10 %, 200–600 μm 14 %, 600–2,000 μm 4 %, >2,000 μm 3 %; TOC acc. DIN EN 13137: 15 % w/w dm; heavy metals in the fraction <20 μm acc. DIN EN ISO 11885-E22 based on dry mass: arsenic 116 mg/kg, lead 978 mg/kg, cadmium 20 mg/kg, chrome 152 mg/kg, copper 450 mg/kg, nickel 96 mg/kg, zinc 2,460 mg/kg; mercury acc. DIN EN 1483-E12: 16 mg/kg; petroleum-derived hydrocarbon acc. DIN ISO 16703: 33 g/kg w/w dm; sum chlorobenzene analog to DIN EN ISO 6468-F1: 624 μg/kg dm; sum polychlorinated biphenyls analog to DIN 38414–20, DIN 38407–2: 300 μg/kg dm; hexachlorocyclohexane analog to DIN 38414–20, DIN 38407–2: α-HCH: 18 μg/kg dm, β-HCH: <0.2 μg/kg dm, γ-HCH 13 μg/kg dm: polycyclic aromatic hydrocarbons (sum PAH EPA) via GC-MSD acc. Merkbl. 1 LUA-NRW: 5,260 mg/kg dm).
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Acknowledgments
We would like to thank Bernd Uebelmann and Shane Denecke for linguistic comments. The views and conclusions contained in this paper are those of the authors and should not be interpreted as representing the opinions or policies of the German Federal Institute of Hydrology (BfG) or the German Government.
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Siebeneicher, S., Wahrendorf, DS., Wetzel, M.A. et al. Analysis of burrowing ability as a sublethal endpoint in a marine sediment bioassay with Corophium volutator (Pallas). J Soils Sediments 13, 197–206 (2013). https://doi.org/10.1007/s11368-012-0619-5
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DOI: https://doi.org/10.1007/s11368-012-0619-5