Research in Estuarine Ecosystems: Various Harmful Species in the Neuse Estuary
A recent Ph.D. dissertation completed at the CAAE used a continuous, 13- year record of environmental data and phytoplankton taxa in the mesohaline estuary (1994-2006; biweekly, April-October; monthly, November-March) to evaluate phytoplankton assemblage responses to changing environmental conditions. Ordination techniques including non-metric multidimensional scaling (NMDS), indicator species analysis, and BIOENV software were used to investigate potential environmental predictors of phytoplankton assemblage patterns under chronic eutrophication (see Rothenberger et al., Limnol. Oceanogr. 54: 2107-2127).
The CAAE has also characterized blooms in the Neuse Estuary that have been dominated or co-dominated by Prorocentrum minimum (e.g. see Springer et al. 2005, Harmful Algae 4: 533-551). The developing bloom was first detected from a web-based alert provided by the Center’s real-time remote monitoring (RTRM) platforms, indicating elevated dissolved oxygen (DO) and pH levels in the upper estuary. These data were used to augment shipboard sampling in characterizing bloom initiation, development, movement, and dissipation over a 7-month period (October 2001-April 2002).
Chlorophyll a (chla) within bloom areas averaged 106 +13 μg L-1 (mean + 1 SE), with a maximum of 803 μg L-1, in comparison to 20 μg L-1 outside the bloom. There were significant positive relationships between dinoflagellate abundance and TN and TP. NH4 +, NO3 -+NO2 -, and soluble reactive phosphorus (SRP) concentrations did not decrease within the main bloom, suggesting that upstream inputs and other sources provided nutrientreplete conditions. In addition, PAM fluorometric measurements (at 0900-1300 hours) of maximal PSII quantum yield (Fv/Fm) were consistently 0.6-0.8 within the bloom until late March, providing little evidence of photophysiological stress as would have been expected under nutrient-limiting conditions. An analysis of N uptake kinetics during the period when P. minimum was dominant (October- December) suggested that NH4 + was the major N species that supported the bloom. Bloom displacement (January-February) coincided with higher diversity of heterotrophic dinoflagellate species as P. minimum abundance decreased.