Physiological effects of the detergent linear alkylbenzene sulphonate on blue mussel larvae (Mytilus edulis) in laboratory and mesocosm experiments |
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Authors: | B Hansen F L Fotel N J Jensen L Wittrup |
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Institution: | (1) Roskilde University, Department of Life Sciences and Chemistry, P.O. Box 260, DK-4000 Roskilde, Denmark, DK |
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Abstract: | A series of laboratory (short-term exposure in small beakers) studies and a 19 d mesocosm (6 m3 polyethylene bags filled with fjord water) study were conducted on blue mussel, Mytilus edulis, larvae and plantigrades exposed to a concentration gradient of the detergent linear alkylbenzene sulphonate (LAS, 0 to 39 mg l−1). LAS is increasingly found in nearshore environments receiving wastewater from urban treatment plants. The aims were to
observe physiological effects on swimming, grazing and growth in the laboratory and effects on settling and population development
at in situ conditions (in field mesocosms) in order to evaluate the damages on ciliated meroplankton caused by LAS. In the
laboratory the larvae showed a 50% mortality at 3.8 mg LAS l−1 after 96 h exposure whether or not food was provided. Additionally the swimming behaviour was affected at 0.8 mg LAS l−1 (i.e. a more compact swimming track, a smaller diameter of the swimming tracks, and reduced swimming speed). The larval particle
grazing was reduced 50% at 1.4 mg LAS l−1. The specific growth rate of the larvae was reduced to half at 0.82 mg LAS l−1 over 9 d. During the mesocosm experiment, the larval population showed a dramatic decrease in abundance within 2 d at concentrations
as low as 0.08 mg LAS l−1, both due to a significantly increased mortality, but also due to settling. The settling success was reduced at the same
LAS concentration as that at which mortality was observed to increase significantly. In addition to reduced settling rate,
the larvae showed delayed metamorphosis and reduced shell growth as a response to LAS. Our hypothesis that the larval ciliary
apparatus, crucial for normal swimming, orientation, and settling behaviours and for particle uptake, was damaged due to LAS
exposure is supported by our results. This is confirmed by the physiological data (grazing, growth) and in the direct video-based
observations of larval performance (swimming) and provides a reasonable explanation for what was observed in the bags (abundance,
settling, mortality). These physiological effects on blue mussel larvae/plantigrades occurred at LAS concentrations reported
to occur in estuarine waters.
Received: 15 January 1997 / Accepted: 12 February 1997 |
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