North Collier County
Marine Investigation

 

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Coastal Planning & Engineering, Inc. (CPE) was selected by Collier County to conduct its largest nearshore hardbottom characterization. The comprehensive marine resources investigation was carried out along the county’s nearshore habitat between Florida Department of Environmental Protection (FDEP) survey control monuments R-17 and R-89, along approximately 13.5 miles of coastline. A side-scan sonar survey of the nearshore region of the study area for Collier County in February 2003 documented the presence of coastal low relief ephemeral hardbottom habitats that may be affected by beach nourishment activities. Approximately 500 acres of hardbottom formations were identified within 1,000 ft of the shoreline along the 13.5 mile long study area.

The focus of the investigation was assessment and characterization of the nearshore hardbottom resources which may be within the zone of influence of the beach nourishment project, cross-shore beach profile adjustment, or long-shore fill diffusion. All work was conducted within 300 m of shore. A total of 68 hardbottom sites (60 transects and 8 points) directly offshore of Collier County were selected for exploratory verification, assessment, and characterization in coordination with the Florida Department of Environmental Protection (FDEP). These 68 sites were sorted into six study segments; Delnor-Wiggins State Park (9 transects and 2 points), Vanderbilt Beach (10 transects and 3 points), Pelican Bay (6 transects), Clam Pass Park (10 transects), Park Shore (17 transects and 2 points), and Naples (8 transects and 1 point).

Benthic communities along transects were evaluated using both a modification of the Atlantic and Gulf Rapid Reef Assessment (AGRRA) protocol (Ginsburg, 2000) and GPS-integrated video surveys. AGRRA methods were employed at 638 quadrats covering a total of 319 m2. An extensive database of assessments and identifications was created to include both biotic factors (coral density, macroalgae cover, fish identifications) and abiotic factors (sediment depth, substrate type, substrate relief), supplemented with a photographic library comprised of over 1100 still images and 64 videos.

The segment averages varied widely, with generally greater biotic cover and relief towards the north, and greater sand cover towards the south. The overall frequency of quadrats with 100% sand cover was 0.32. At least one-third of the study area was sand covered, and the remaining two-thirds were partly or completely exposed hardbottom. The data sorted segments into three relatively distinct groups. The two northernmost segments had relief, sediment, and biotic cover close to the overall averages. The two central segments had the greatest relief, low sediment, and high biotic cover. The two southernmost segments had the lowest relief, greatest sediment cover, and lowest biotic cover of all segments. Generally, macroalgae percent cover was negatively correlated with both sand cover and average sediment depth. The two most dominant macroalgae genera were Gracilaria, and Hypnea. Both are known to be consumed by juvenile green sea turtles. Caulerpa spp., Sargassum spp., Dasya spp., and Botryocladia occidentalis were occasional.

Gorgonacea were infrequent, with less than one colony encountered per average transect. The transects found more Gorgonacea in the northernmost (0.31 colonies m-2) and southernmost segments (0.23 colonies m-2). Within these segments, distribution of Gorgonacea was patchy, and ranged from zero to 1.09 colonies m-2. Gorgonacea were essentially absent from the four interior segments, Vanderbilt Beach, Pelican Bay, Clam Pass Park, and Park Shore. Those encountered loosely followed shore-parallel distribution patterns, and were likely underreported by conducting shore-perpendicular transects.

Scleractinia density was surprisingly high for this turbid nearshore habitat. The vast majority of coral records were Siderastrea spp., and three other genera were occasional; Oculina sp., Phyllangia sp., and Solenastrea sp. There were approximately twice as many Scleractinia colonies m-2 in the northern three segments than in the southern three segments. This survey found anomalously few <2 cm colonies relative to 2-5 cm colonies. The size-frequency results suggest that the nearshore habitat was chronically disturbed with respect to Scleractinia in the last decade or so. There was a loose negative correlation between Scleractinia density and both sediment depth and sand cover. Because mobile sediment effectively prevents Scleractinia larvae recruitment, mobile sediment may be greater today than decades ago.

During the fish surveys, twenty-one species were noted. The highest number of species (14) was recorded in the Park Shore Segment, though this high number is biased by the larger size of the Park Shore Segment. The Pelican Bay Segment supported the second highest number of species (10).

CPE has developed an inclusive database, and archived all field data into an easily accessible GIS product with tables, representative imagery, and video documentation that allows users to evaluate information themselves. The Collier County database will continue to grow with future monitoring and documentation, providing accurate temporal analysis of the nearshore habitat.

CPE’s uniquely thorough exploratory hardbottom characterizations have developed into a substantial database. We now know that the Collier County nearshore hardbottom has greater biotic cover than hardbottom analogues on Florida’s south and east coasts.

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Pictures

Image from transect R21+460 in the Delnor-Wiggins State Park segment. This colony of Solenastrea hyades (side-view) was one of the largest coral colonies found in the nearshore hardbottom
Image from transect R21+460 in the Delnor-Wiggins State Park segment. This colony of Solenastrea hyades (side-view) was one of the largest coral colonies found in the nearshore hardbottom

Image from transect R21+460 in the Delnor-Wiggins State Park segment. This colony of Solenastrea hyades (overhead-view) was one of the largest coral colonies found in the nearshore hardbottom
Image from transect R21+460 in the Delnor-Wiggins State Park segment. This colony of Solenastrea hyades (overhead-view) was one of the largest coral colonies found in the nearshore hardbottom

Image from transect R23+285 in the Delnor-Wiggins State Park segment. This colony of Oculina robusta was exceptional in the nearshore, and typical of the hardbottom 2-3 miles offshore
Image from transect R23+285 in the Delnor-Wiggins State Park segment. This colony of Oculina robusta was exceptional in the nearshore, and typical of the hardbottom 2-3 miles offshore

Image from transect R28+450 in the Vanderbilt Beach segment. High algae cover is typical of the nearshore hardbottom
Image from transect R28+450 in the Vanderbilt Beach segment. High algae cover is typical of the nearshore hardbottom

Image from transect R29+700 in the Vanderbilt Beach segment. It is unclear whether the color difference between these two Siderastrea sp. colonies is a sign of stress or a simple difference between individuals
Image from transect R29+700 in the Vanderbilt Beach segment. It is unclear whether the color difference between these two Siderastrea sp. colonies is a sign of stress or a simple difference between individuals

Image from transect R29+700 in the Vanderbilt Beach segment. This quadrat is 0.50 square-meters. High algae cover is typical of the nearshore hardbottom
Image from transect R29+700 in the Vanderbilt Beach segment. This quadrat is 0.50 square-meters. High algae cover is typical of the nearshore hardbottom

Image from transect R29+700 in the Vanderbilt Beach segment. Three coral species, Siderastrea sp., Oculina robusta, and Solenastrea hyades
Image from transect R29+700 in the Vanderbilt Beach segment. Three coral species, Siderastrea sp., Oculina robusta, and Solenastrea hyades

Image from transect R30+520 in the Vanderbilt Beach segment. Nearly 100% macroalgae cover was relatively common in the nearshore hardbottom
Image from transect R30+520 in the Vanderbilt Beach segment. Nearly 100% macroalgae cover was relatively common in the nearshore hardbottom

Image from transect R31+480 in the Pelican Bay segment. This image shows relatively high relief for the nearshore hardbottom, 35 cm (14 inches)
Image from transect R31+480 in the Pelican Bay segment. This image shows relatively high relief for the nearshore hardbottom, 35 cm (14 inches)

Image from transect R31+480 in the Pelican Bay segment
Image from transect R31+480 in the Pelican Bay segment

Image from transect R31+480 in the Pelican Bay segment. This quadrat is 0.50 square-meters. This view is typical of the nearshore habitat in the Pelican Bay segment
Image from transect R31+480 in the Pelican Bay segment. This quadrat is 0.50 square-meters. This view is typical of the nearshore habitat in the Pelican Bay segment

Image from transect R33 in the Pelican Bay segment. This extraordinary colony of Oculina robusta was a surprising find in the nearshore hardbottom
Image from transect R33 in the Pelican Bay segment. This extraordinary colony of Oculina robusta was a surprising find in the nearshore hardbottom


Image from transect R65 in the Naples segment. Reef fish were common in the nearshore hardbottom, but were very difficult to observe because visibility was typically poor

Image from transect R65 in the Naples segment. Reef fish were common in the nearshore hardbottom, but were very difficult to observe because visibility was typically poor
Image from transect R65 in the Naples segment. Reef fish were common in the nearshore hardbottom, but were very difficult to observe because visibility was typically poor

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 2481 N. W. Boca Raton Blvd., Boca Raton, Florida 33431(561) 391.8102 (561) 391.9116email@coastalplanning.net