Barnegat Bay-Little Egg Harbor Research Articles

Seagrass Habitat Characterization in Estuarine Waters of the Jacques Cousteau National Estuarine Research Reserve Using Underwater Videographic Imaging Techniques

A benthic habitat assessment study conducted in the Barnegat Bay-Little Egg Harbor Estuary from June to November 2006 reveals that boat-based videographic imaging is comparable to in situ diver observations for determining the occurrence and percent cover of seagrasses in actively growing beds. A Seaviewer Sea Drop camera and recorder unit deployed along 12 transects in the estuary generated 331 images of seagrass habitat during the study period. A comparison of video still images with data derived from diver observations indicates consistent results in terms of the presence/absence and percent cover of seagrass on the estuarine floor throughout the seagrass growing season. Plots of the percent cover of seagrass recorded by the camera system vs. in situ diver observations reveal a high correlation for the June–July, August–September, and October–November sampling periods (R2 = 0.936, 0823, and 0.894, respectively) as well as for the entire June–November sampling period (R2 = 0.888). A kappa statistic calculated for the presence/absence of seagrass in the estuary (0.83) reflects a nearly perfect level of agreement between the two methods (camera and diver) of data collection. In addition to generating rapid databases, digital underwater video imaging requires less field time than the use of divers and other traditional field monitoring methods. Digital videographic files can also be post-processed, geolocated using a global positioning system, analyzed by multiple investigators, and stored for later analysis, thereby offering several other advantages over traditional in situ monitoring techniques in shallow estuarine systems.

Status of organic pollutants in surface sediments of Barnegat Bay-Little Egg Harbor Estuary, New Jersey, USA

Numerous surveys have demonstrated that diffuse pollution from urban-residential run-off and industrial discharges can adversely impact salt marsh and tidal creek sediment quality (Barrett & McBrien, 2006; Fox et al., 2001; Iannuzzi et al., 1995; Long et al., 1995; Sanger et al., 2004; White et al., 2005). The impact of shipping activities, including major discharge of fuel oil onto salt marshes, has also been reported (White et al., 2005). However, few studies have assessed organic pollution accumulating in salt marshes with watersheds that are mainly comprised of forests and wetlands but which have major residential areas located off-shore of the mainland. The salt marshes of Barnegat Bay-Little Egg Harbor Estuary, southeast New Jersey represent one such geographical setting (Fig .1). The shallow (17 m), narrow (3-9 mile) bay is separated from the Atlantic Ocean by a back barrier island complex (Long Beach Island) which is heavily developed and a major area of tourism (Fig. 1). The salt marshes are protected and managed as part of the Edwin B. Forsythe National Wildlife Refuge, this comprises 186 km of wetlands and 145 km of salt marshes and has a mixed pattern of watershed land use such as forestry (45.9 %), wetlands (25.2 %), urban/residential (19.5 %) and agricultural (6.6 %).

Assessment of brown tide blooms, caused by Aureococcus anophagefferens, and contributing factors in New Jersey coastal bays: 2000–2002

A 3 year study (2000–2002) in Barnegat Bay-Little Egg Harbor (BB/LEH), New Jersey (USA), was conducted by the New Jersey Department of Environmental Protection, Division of Science Research and Technology (DSRT) in cooperation with several partners to assess brown tide blooms in coastal waters in NJ. Water samples were collected by boat and helicopter at coastal stations from 2000 to 2002 along with field measurements. Aureococcus anophagefferens were enumerated and associated environmental factors were analyzed. A. anophagefferens abundances were classified using the Brown Tide Bloom Index and mapped, along with salinity and temperature parameters, to their geo-referenced location using the ArcView GIS. The highest A. anophagefferens abundances (>10 6 cells ml −1), including category 3 blooms (≥200,000 cells ml −1) and category 2 blooms (≥35,000 to ≤200,000 cells ml −1), recurred during each of the 3 years of sampling and covered significant geographic areas of the estuary, especially in Little Egg Harbor. While category 3 blooms were generally associated with warmer water temperatures (>16 °C) and higher salinity (>25–26 ppt), these factors were not sufficient alone to explain the timing or distribution of A. anophagefferens blooms. There was no significant relationship between brown tide abundances and dissolved organic nitrogen measured in 2002 but this was consistent with other studies. Extended drought conditions, with corresponding low freshwater inputs and elevated bay water salinities, occurring during this time were conducive to blooms. A. anophagefferens abundances were well above the reported levels that have been reported to cause negative impacts on shellfish. It was shown that over 50% of the submerged aquatic vegetation (SAV) habitat located in Barnegat Bay/Little Egg Harbor was categorized as having a high frequency of category 2 or 3 blooms for all 3 years.