Abstract
Swimming behaviour was investigated in adult egg-carrying northern shrimp (Pandalus borealis) exposed to dilute concentrations of the pesticides Alpha Max® (active ingredient deltamethrin) and Salmosan® (active ingredient azamethiphos) used to control parasitic copepods in salmon aquaculture. These treatments are applied topically within fish nets or well boats. Following a short treatment period, the pesticides are directly discharged to sea, exposing non-target organisms such as P. borealis to diluted concentrations of these chemicals. Locomotor activity was measured continuously in individual shrimp over several days within which they were exposed to treatments of diluted AlphaMax® or Salmosan®. Dilutions were based on modelling and dispersion studies from the literature and were considered environmentally realistic for greater than 1km from point of discharge. 24h continuous flow treatments were delivered within a 3.5-day monitoring period to observe the timeline of events following the release of treatment water, addressing questions of temporal responses in locomotor activity, recognising key time points of significant events and assessing the survival capacity of the shrimp. Exposure of shrimp to 1ng l-1 deltamethrin triggered an immediate increase in swimming activity which reduced in intensity over the following 22h leaving all shrimp either moribund or dead. A further exposure trial exposing shrimp to 0.2ng l-1 deltamethrin (nominal) showed an increase in activity at the start of exposure that continued throughout the 24h delivery, returning to previous levels by the end of the 3.5-day monitoring period. All these shrimps survived for at least four weeks after exposure, putting the threshold concentration of deltamethrin leading to immobility or death in adult P. borealis within this study at greater than 0.2ng l-1 (nominal) and less than 1ng l-1 (measured). Exposure of P. borealis to azamethiphos at 30ng l-1 induced several periods of significantly increased activity within the first 10h of exposure and an extended period of reduced activity during post exposure, though no morbidity was observed with this treatment. No significant increase in activity or morbidity was observed in shrimp during a water vehicle control assessment. Shrimps exposed to a combination of 30ng l-1 azamethiphos and 1ng l-1 deltamethrin broadly followed the response pattern shown by shrimp exposed to 1ng l-1 deltamethrin alone. Pesticide residues were not detected in post exposure tissue analyses for either chemical. The potential ecological significance of increased swimming activity at the start of pesticide exposures is discussed.
Highlights
Salmon lice remain a major challenge for open water pen salmon aquaculture
Coastal fjords are popular locations for open water salmon farming in Norway and these areas are often the habitat of the northern shrimp (Pandalus borealis), a species with both ecological and commercial value (Bergstrom, 2000). This present study has examined the responses of adult egg carrying P. borealis in the laboratory following their exposure to dilute concentrations of two neurotoxic pesticides used in salmon lice control, AlphaMax® and Salmosan®
Analysis of shrimp tissue samples taken at the end of the 1 ng l− 1 exposure did not detect the presence of deltamethrin
Summary
Salmon lice remain a major challenge for open water pen salmon aquaculture. These ectoparasitic copepods cause damage to the skin of their hosts that can lead to imbalances in physiological processes and provide a gateway for disease with the result that both fish welfare and productivity of the aquaculture facility are reduced (Thorstad and Fin stad, 2018; Bowers et al, 2000). Operational constraints on the exposure time for treating salmon with topical pesticides demands that relatively high concentrations of these chemicals are used to ensure their efficacy against the parasitic copepod target. Chemical treatments can be repeated over time and it is recommended to avoid the use of combinations of pesticides for single pen treatments (Grefsrud et al, 2018), discharges from farms within the same region applying different chemical treatments can potentially generate combinations of pesticides within the surrounding water masses (Grefsrud et al, 2018)
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