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Benthic Foraminiferal Community Changes Across the Miocene Climatic Optimum Identified by Shebi Analysis (She Analysis for Biozone Identification), Calvert Cliffs, Maryland, USA
Benthic Foraminiferal and Sedimentologic Changes in the Pliocene Yorktown Formation, Virginia, USA
CHARACTERIZING MODERN AND HOLOCENE BARRIER-ISLAND ENVIRONMENTS WITH FORAMINIFERAL ASSEMBLAGES: AN EXAMPLE FROM A WAVE-DOMINATED, MICROTIDAL BARRIER-ISLAND SYSTEM, NORTH CAROLINA, USA
MIOCENE NERITIC BENTHIC FORAMINIFERAL COMMUNITY DYNAMICS, CALVERT CLIFFS, MARYLAND, USA: SPECIES POOL, PATTERNS AND PROCESSES
Distribution of Foraminifera off the Terengganu River Mouth, East Coast Peninsular Malaysia
Rapid Change of Foraminiferal Communities and Assemblages in the Setiu Estuary, Terengganu, Malaysia: Anthropogenic Drivers
ABSTRACT The distribution and taxonomy of modern benthic foraminifera are described for the western Sunda Shelf, southern South China Sea off northeast peninsular Malaysia. This study provides baseline foraminiferal data that can be utilized in paleoenvironmental reconstructions of Neogene sediments from the Sunda Shelf and elsewhere in the Indo-Pacific. The uppermost centimeter of 60 surface sediment samples (> 150 µm) from nearshore (8 m) to inner shelf (60 m) water depths yielded 125 species. The distribution of these species is described and 120 species are illustrated with color light microscope digital images and scanning electron microscope imagery. Five sample assemblages, CGT1-CGT5 are interpreted from the results of the cluster analysis of total (live plus dead) foraminiferal relative abundance data. Discriminant analysis demonstrates that these five groups are statistically distinguishable at the 95% confidence level. The distribution of groups is related to variations in depth and substrate grain-size. This relationship is reaffirmed by canonical correspondence analysis. Closest to shore (8–14 m water depth), the high diversity (49 species) assemblage (CGT1), characterized by Amphistegina radiata and Amphistegina lessonii , occurs in medium to coarse quartz sand substrates, likely derived from the nearby Terengganu River. In slightly deeper water (21–22 m) and in gravelly quartz sand substrates, the lower diversity (33 species) assemblage of CGT2 is strongly dominated by Amphistegina radiata and Amphistegina lessonii . CGT3 occurs in shelly muddy quartz sand substrates (32–41 m), has a high diversity assemblage (46 species), and is characterized by Assilina ammonoides , Amphistegina radiata and Discorbinella bertheloti . Berthierine internal molds of Amphistegina lessonii and Amphistegina radiata are common in CGT1, CGT2 and CGT3, possibly indicating reworking from Pleistocene deposits in the region. High diversity (51 species) assemblage CGT4 occurs in mud substrates (44–59 m) and is characterized by Heterolepa dutemplei and Asterorotalia milletti ; the nearshore, sandy substrate taxa Amphistegina radiata and Amphistegina lessonii are absent. CGT5, located farthest from shore at 60 m water depth and in shelly sandy mud and shelly muddy sand, has a high diversity assemblage (46 species) characterized by Heterolepa dutemplei and Assilina ammonoides , with rare Asterorotalia milletti . This assemblage may be, in part, a lag deposit associated with modern bottom currents. The results of this study were combined with previously published research to identify nine foraminifera-based environmental subdivisions in the southern South China Sea: mangrove swamps in Terengganu and Sabah, Malaysia; high salinity lagoonal and inlet assemblages in Terengganu, Malaysia; low salinity estuarine assemblages in Terengganu, Malaysia; Mekong Delta assemblages; nearshore areas in the northern Gulf of Thailand off the mouths of rivers; inner shelf environments off the Mekong delta and off Johore, Malaysia dominated by Asterorotalia pulchella ; shallow inner shelf (<40 m water depth) environments from Terengganu and Johore, Malaysia; inner shelf environments (40–100 m water depth) off Terengganu, Malaysia and on the east-central Sunda Shelf; outer shelf environments (100–200 m water depth) on the east-central Sunda Shelf. The subdivisions are related mainly to salinity in marginal marine environments and substrate type and depth/distance from shore in shelf environments.
THE INFLUENCE OF AQUACULTURE ON MODERN FORAMINIFERA AND SEDIMENTS IN THE SETIU ESTUARY AND LAGOON, TERENGGANU, MALAYSIA: A TEMPORAL INVESTIGATION
THE INFLUENCE OF AQUACULTURE ON MODERN FORAMINIFERA AND SEDIMENTS IN THE SETIU ESTUARY AND LAGOON, TERENGGANU, MALAYSIA: A SPATIAL INVESTIGATION
Graphic Logging For Interpreting Process-Generated Stratigraphic Sequences and Aquifer/Reservoir Potential: With Analog Shelf To Shoreface Examples From the Atlantic Coastal Plain Province, U.S.A
INFAUNAL MANGROVE SWAMP FORAMINIFERA IN THE SETIU WETLAND, TERENGGANU, MALAYSIA
Standardizing Texture and Facies Codes for A Process-Based Classification of Clastic Sediment and Rock
DISTRIBUTION OF FORAMINIFERA IN THE SETIU ESTUARY AND LAGOON, TERENGGANU, MALAYSIA
MODERN FORAMINIFERAL DISTRIBUTION AND RECENT ENVIRONMENTAL CHANGE IN CORE SOUND, NORTH CAROLINA, USA
Eye of a human hurricane: Pea Island, Oregon Inlet, and Bodie Island, northern Outer Banks, North Carolina
Pea Island, Oregon Inlet, and Bodie Island, North Carolina, are severely human-modified barrier-island segments that are central to an age-old controversy pitting natural barrier-island dynamics against the economic development of coastal North Carolina. Bodie Island extends for 15 km from the Nags Head–Kitty Hawk urban area to the north shore of Oregon Inlet and is part of Cape Hatteras National Seashore. Pea Island extends 19.3 km from the southern shore of Oregon Inlet to Rodanthe Village and is the Pea Island National Wildlife Refuge. Bodie and Pea Islands evolved as classic inlet- and overwash-dominated (transgressive) simple barrier islands that are now separated by Oregon Inlet. The inlet was opened in 1846 by a hurricane and subsequently migrated 3.95 km past its present location by 1989. With construction of coastal Highway 12 on Bodie and Pea Islands (1952) and the Oregon Inlet bridge (1962–1963), this coastal segment has become a critical link for the Outer Banks economy and eight beach communities that occur from Rodanthe to Ocracoke. The ongoing natural processes have escalated efforts to stabilize these dynamic islands and associated inlet in time and space by utilizing massive rock jetties and revetments, kilometers of sand bags and constructed dune ridges, and extensive beach nourishment projects. As the coastal system responds to ongoing processes of rising sea level and storm dynamics, efforts to engineer fixes are increasing and now constitute a “human hurricane” that pits conventional utilization of the barriers against the natural coastal system dynamics that maintain barrier-island integrity over the long term.