Serum ammonium concentrations ranged between ca. 220 and
830 μM, with generally lower concentrations found in the depurated
treatments at the pre- and post-rewatering stage (Fig. 2B). After the
grading process, mussel serum ammonia was 311 μM. This decreased
significantly for mussels in the depurated treatment and increased
significantly for non-depurated mussels (238 and 500 μM respectively;
ANOVA, P b 0.05). Post-transport, serum ammonium remained low
for depurated mussels (under 555 μM) whilst in comparison, nondepurated
mussels experienced a significant increase in serum
ammonia irrespective of transport temperature (688–838 μM; ANOVA,
P b 0.05–0.001). Mussels transported on ice showed a trend for
increased ammonium concentration compared to their non-iced counterparts;
for depurated mussels, this trend was significant (ANOVA,
P b 0.01). Post-rewatering serum ammonium concentrations fell to
under ca. 330 μM, not significantly different between treatments.
Serum ammonium concentrations ranged between ca. 220 and830 μM, with generally lower concentrations found in the depuratedtreatments at the pre- and post-rewatering stage (Fig. 2B). After thegrading process, mussel serum ammonia was 311 μM. This decreasedsignificantly for mussels in the depurated treatment and increasedsignificantly for non-depurated mussels (238 and 500 μM respectively;ANOVA, P b 0.05). Post-transport, serum ammonium remained lowfor depurated mussels (under 555 μM) whilst in comparison, nondepuratedmussels experienced a significant increase in serumammonia irrespective of transport temperature (688–838 μM; ANOVA,P b 0.05–0.001). Mussels transported on ice showed a trend forincreased ammonium concentration compared to their non-iced counterparts;for depurated mussels, this trend was significant (ANOVA,P b 0.01). Post-rewatering serum ammonium concentrations fell tounder ca. 330 μM, not significantly different between treatments.
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