Biodiversity of the Caribbean

Total Page:16

File Type:pdf, Size:1020Kb

Biodiversity of the Caribbean Biodiversity of the Caribbean A Learning Resource Prepared For: (Protecting the Eastern Caribbean Region’s Biodiversity Project) Photo supplied by: Andrew Ross (Seascape Caribbean) Part 2 / Section C Coral Reef Ecosystems February 2009 Prepared by Ekos Communications, Inc. Victoria, British Columbia, Canada [Part 2/Section C] Coral Reef Ecosystems Table of Contents C.1. What is a Coral Reef Ecosystem? C.2. Formation of Coral Reefs C.3. Types of Coral Reefs C.4. Species Biodiversity C.5. Importance of Coral Reefs C.5.a. Food Source and Habitat C.5.b. Water Filtration C.5.c. Fisheries C.5.d. Tourism C.5.e. Coastal Protection C.5.f. Source of Scientific Advances C.5.g. Intrinsic Value C.6. Types of Human & Natural Impacts C.6.a. Pollution C.6.b. Over-fishing C.6.c. Tourism C.6.d. Sedimentation C.6.e. Mining Reef Resources C.6.f. Climate Change C.7. Protecting Coral Reefs C.8. Student Fact Sheet: Fifty Facts About Wider Caribbean Coral Reefs C.9. Case Study: Tobago Cays Marine Park (TCMP), Southern Grenadines C.10. Activity 1: Mock Marine Management Plan C.11. Activity 2: Coral Reef Ecosystem Poster Presentation C.12. Case Study: Community-Based Natural Resource Management in the Bay Islands, Honduras C.13. Activity 3: Diagram the Case! C.14. References [Part 2/Section C] Coral Reef Ecosystems C.1. What is a Coral Reef Ecosystem? 30°C. Tropical corals are found within three main regions of the Coral reefs exist in the warm, clear, shallow waters of tropical world: the Indo-Pacific, the Western North Atlantic, and the Red oceans worldwide but also in the cold waters of the deep seas. Sea. The Western North Atlantic region contains the second most For the purpose of this section, the marine, warm water coral coral reefs (after the Indo-Pacific) and includes the coral reefs reefs will be discussed. within the Caribbean. Types of Corals There are two main types of corals: hard corals composed of C.2. Formation of Coral Reefs stony calcium carbonate, and soft corals composed of a protein Coral reefs are formed by the work of tiny organisms known as and calcium carbonate material. Solid corals, or Scleractinians, coral polyps. A coral polyp consists of a fleshy sack with a ring including brain, star, staghorn, elkhorn, and pillar corals have of tentacles that sits in a limestone skeletal case, secreted by the rigid exoskeletons that protect their soft interiors. Soft corals, or polyp. Thousands of coral polyps develop together and create a Gorgonians, including sea fans, sea whips, and sea rods, sway structure of limestone (calcium carbonate or CaCO3). The prime with the ocean currents and lack a stony exoskeleton. reef builders are the stony or hard corals (Anthozoa species). The bulk of any reef colony is composed of nonliving matter. It 4 Tropical coral reefs occupy less than one percent of the Earth’s is only the upper layer that is living cora l. While corals are the marine environment, but are home to more than a quarter of all chief architects of reef structure, they are not the only builders. known marine fish species and tens of thousands of other species Coralline algae cement various corals together with compounds found nowhere else on earth1. The total area of the world’s tropi- of calcium, and other organisms such as tube worms and mol- 5 cal coral reefs is around 284,300km². 2 Of the total amount of luscs donate their hard skeletons . Tropical coral reefs can grow coral reefs in the world, 7.64% of it is located within the Carib- upwards at rates of 1centimetre to 100 centimetres per year. bean Sea Large Marine Ecosystem3. This is in contrast to deep sea corals which grow a mere 5 to 25 millimetres each year. For both coral types, over time they form Factors Necessary for the Formation of extensive reefs. Coral Reefs Reef-building corals have evolved an essential symbiotic Geographically, tropical coral reefs lie between the latitudes of relationship with a type of brown algae called zooxanthellae 30 degrees north and south where sea temperatures are warmest. (Symbiodinium microadriaticum). A symbiotic relationship ex- Tropical coral reefs require water temperatures between 18°C and ists where two or more organisms co-exist together in a mutually advantageous relation- ship, with both deriv- ing benefits from each other. Millions of these single-celled algae are living as symbionts within their tissues of corals. Zooxanthellae produce sugars and oxygen through photo- synthesis which helps the coral in the process of producing limestone or calcium carbonate. With this assistance by zooxanthellae, corals grow up to three times faster. It is also the zooxanthellae, which give the corals their characteristic greenish color. In the case of a change in environmen- tal conditions, such as increased temperatures or changes in salinity, World Resources Institute. (2004). Reefs at risk in the Caribbean. Retrieved from: arthtrends.wri.org/features/view_feature.php?fid=55&theme=1 the coral polyps may expel the algae. Without [Part 2/Section C] Coral Reef Ecosystems Zubi, T. (2008). Coral reef ecology. Retrieved from: starfish.ch/reef/reef.html algae, the coral becomes completely white in colour and is con- Coral reefs rank among the largest and oldest sidered bleached. If the coral retains some algae it may survive, living communities of plants and animals on but if bleaching occurs the coral is considered dead. Earth, with the most established coral reefs be- 6 ginning to grow 5000-10,000 years ago . Tropical corals require access to sunlight to survive. The algae living in their cells require light for photosynthesis. Because of this, the water where they grow needs to be shallow and clear. High levels of sediment in the water can smother the coral pol- yps. Corals also require salt water, and the lowering of salinity in their marine habitat can kill them. Essentially, coral development occurs away from river mouths and other sources of fresh water. C.3. Types of Coral Reefs There are four different types of coral reefs: fringing reefs, platform reefs, barrier reefs, and atolls. Reefs that grow in shallow waters are classified as fringing reefs. These reefs border the coast of tropical islands or continents closely or are separated from the coast by a narrow stretch of water. Fringing reefs are generally narrow platforms a short distance from shore and don’t contain a substantial lagoon. Fringing coral reef communities are found in places on the shores of most of the islands in the Eastern Caribbean. Platform reefs develop in sheltered seas, but quite far offshore. They are flat-topped with small and shallow lagoons. Barrier reefs are reefs that are grow parallel to the coast but are separated from land by a lagoon. As the reef continues to grow and moves further offshore, it eventually reaches the edge of the continental shelf (the region of relatively shallow water sur- Photo supplied by: Andrew Ross (Seascape Caribbean) rounding every continent). Barrier reefs can originate offshore if [Part 2/Section C] Coral Reef Ecosystems Coral Reefs in Belize the depth of the seabed is shallow enough to give corals sufficient light to develop. The two largest barrier reefs are the Great Barri- Belize boasts the second largest continuous reef system in the er Reef in Australia, which stretches over 2300 kilometres off the Western Hemisphere, second only to Australia’s Great Bar- coast of Queensland in northeast Australia, and the Mesoameri- rier Reef. The reef of Belize stretches 250 kms along the entire can reef in the Caribbean, which stretches nearly 250 kilometres length of the country and it encloses an approximately 6000 sq. from the northern tip of Mexico’s Yucatan Peninsula to the Bay km lagoon. Islands in northern Honduras. Atolls are rings of reef, often encircling an island of sand and coral rubble. They typically have a shallow, sandy, sheltered la- goon in the centre and access to the open sea is through a number of channels. These channels provide fresh, colder water to the inside lagoons. Coral atolls begin as fringing reefs around active oceanic volcanoes. After volcanic eruptions cease, an island remains. Over long geologic periods, fringing coral continues to grow and develop into a circular coral reef, which is known as an atoll. Barrier Reef Atoll Fringing Reef Platform Reef Zubi, T. (2008). Coral reef ecology. Retrieved from: starfish.ch/reef/reef.html [Part 2/Section C] Coral Reef Ecosystems C.4. Species Biodiversity (Carangidae) and snappers (Lutjanidae), as well as the Caribbean Coral reefs are one of the most biodiversity-rich ecosystems in reef shark (Carcharhinus perezii), come into coral reefs to prey the world. The Caribbean boasts the highest coral reef diversity on smaller fish species. in the Atlantic Ocean due to its geographic isolation from other oceanic regions7. Staghorn coral (Acropora cervicornis) and elkhorn coral (Acropora palmata) are among the dominant spe- C.5. Importance of Coral Reefs cies living on modern Caribbean reefs. They are particularly fast Coral reefs are often referred to as the “rainforests of the oceans.” growing and able to cope both with damage caused by hurricanes This name is attached to this ecosystem as a result of its role in and by rapid changes in sea level. providing habitat and food for an extensive number of species. Coral reefs host an extraordinary variety of marine plants and Caribbean reefs also house lettuce coral (Agaricia lamarki), star animals (perhaps up to 2 million) including one quarter of all coral (Montastrea faveolata), brain coral (Colpophyllia natans), marine fish species.
Recommended publications
  • Coastal Flood Defences - Groynes
    Coastal Flood Defences - Groynes Coastal flood defences are key to protecting our coasts against flooding, which is when normally dry, low lying flat land is inundated by sea water. Hard engineering methods are forms of coastal flood defences which mitigate the risk of flooding and coastal erosion and the consequential effects. Hard Engineering Hard engineering methods are often used as a temporary measure to protect against coastal flooding as they are costly and only last for a relatively short amount of time before they require maintenance. However, they are very effective at protecting the coastline in the short-term as they are immediately effective as opposed to some longer term soft engineering methods. But they are often intrusive and can cause issues elsewhere at other areas along the coastline. Groynes are low lying wood or concrete structures which are situated out to sea from the shore. They are designed to trap sediment, dissipate wave energy and restrict the transfer of sediment away from the beach through long shore drift. Longshore drift is caused when prevailing winds blow waves across the shore at an angle which carries sediment along the beach.Groynes prevent this process and therefore, slow the process of erosion at the shore. They can also be permeable or impermeable, permeable groynes allow some sediment to pass through and some longshore drift to take place. However, impermeable groynes are solid and prevent the transfer of any sediment. Advantages and Disadvantages +Groynes are easy to construct. +They have long term durability and are low maintenance. +They reduce the need for the beach to be maintained through beach nourishment and the recycling of sand.
    [Show full text]
  • Looe Key Mooring Buoy Service Interrupted July 15-18
    Looe Key Mooring Buoy Service Interrupted July 15-18 Help Us Preserve the Reef The survey requires the same preferred The United States Geological Survey conditions for divers: good visibility and calm (USGS) will be conducting a mission to seas (typical of summer weather) in order to capture high-resolution baseline imagery of establish a high-resolution set of baseline Looe Key reef prior to multi-million dollar images that will allow evaluation of growth of coral restoration efforts taking place under restored corals over time. the Mission: Iconic Reefs initiative. This mission requires the removal of 20 mooring The FKNMS mooring system buoys so the towed, five-camera system (SQUID-5) can safely navigate slow passes Florida Keys National Marine Sanctuary USGS prepares the SQUID-5 for capturing across the entire site, similar to mowing established a mooring buoy program 40 imagery at Eastern Dry Rocks. grass on a football field. The moorings will years ago. Looe Key Sanctuary Preservation be removed on, July 14th and returned to Area features 39 of the nearly 500 first-come, service on July 19th. first-served mooring buoys throughout FKNMS. 14 mooring buoys will remain This activity is a critical part of the $100 available during the survey work. Vessels are million Mission: Iconic Reefs restoration allowed to anchor elsewhere within the program, a partnership between federal, Sanctuary Preservation Area when mooring state and conservation and nonprofit buoys are unavailable--but only on sand. organizations and our local community in one of the largest commitments to coral We are requesting that the public refrain restoration anywhere in the world.
    [Show full text]
  • Coral Reef Fishes Which Forage in the Water Column
    HelgotS.nder wiss. Meeresunters, 24, 292-306 (1973) Coral reef fishes which forage in the water column A review of their morphology, behavior, ecology and evolutionary implications W. P. DAVIS1, & R. S. BIRDSONG2 1 Mediterranean Marine Sorting Center; Khereddine, Tunisia, and 2 Department of Biology, Old Dominion University; Norfolk, Virginia, USA EXTRAIT: <<Fourrages. des poissons des r&ifs de coraux dans la colonne d'eau: Morpholo- gie, comportement, &ologie et ~volution. Dans un biotope ~t r&if de coraiI, des esp&es &roitement li~es peuvent servir d'exempIe de diff~renciatlon sur le plan de t'~volutlon. La radiation ~volutive de poissons repr&entant plusieurs familles du r~eif corallien tropical a conduit ~t plusieurs reprises ~t la formation de <dourragers dans la colonne d'eam>. Ce mode de vie comporte une s~rie de caract~res morphologiques et &hologiques d~finis. On trouve des ~xemples similaires dans I'eau douce et dans des habitats non tropicaux. Les traits distinctifs de cette sp&ialisation, la syst6matique, les caract~rlstiques &ologiques et celies se rapportant ~t l'6volution sont d&rits et discut~s. INTRODUCTION The rapid adoption of in situ studies to investigate lifeways of organisms in the oceans is succeeding in bringing the laboratory to the ocean. Before, the conclusions that observers and scientists were classically forced to accept oPcen represented in- accurate abstractions of things that could not be observed. During the past 10-20 years the cataloging of the fauna and flora of the coral reef habitats has been carried out at an escalated rate, coupled with the many and vast improvements in tools, allowing increased periods of continual observation under sea.
    [Show full text]
  • Spatial and Temporal Distribution of the Demersal Fish Fauna in a Baltic Archipelago As Estimated by SCUBA Census
    MARINE ECOLOGY - PROGRESS SERIES Vol. 23: 3143, 1985 Published April 25 Mar. Ecol. hog. Ser. 1 l Spatial and temporal distribution of the demersal fish fauna in a Baltic archipelago as estimated by SCUBA census B.-0. Jansson, G. Aneer & S. Nellbring Asko Laboratory, Institute of Marine Ecology, University of Stockholm, S-106 91 Stockholm, Sweden ABSTRACT: A quantitative investigation of the demersal fish fauna of a 160 km2 archipelago area in the northern Baltic proper was carried out by SCUBA census technique. Thirty-four stations covering seaweed areas, shallow soft bottoms with seagrass and pond weeds, and deeper, naked soft bottoms down to a depth of 21 m were visited at all seasons. The results are compared with those obtained by traditional gill-net fishing. The dominating species are the gobiids (particularly Pornatoschistus rninutus) which make up 75 % of the total fish fauna but only 8.4 % of the total biomass. Zoarces viviparus, Cottus gobio and Platichtys flesus are common elements, with P. flesus constituting more than half of the biomass. Low abundance of all species except Z. viviparus is found in March-April, gobies having a maximum in September-October and P. flesus in November. Spatially, P. rninutus shows the widest vertical range being about equally distributed between surface and 20 m depth. C. gobio aggregates in the upper 10 m. The Mytilus bottoms and the deeper soft bottoms are the most populated areas. The former is characterized by Gobius niger, Z. viviparus and Pholis gunnellus which use the shelter offered by the numerous boulders and stones. The latter is totally dominated by P.
    [Show full text]
  • Checklist of Fish and Invertebrates Listed in the CITES Appendices
    JOINTS NATURE \=^ CONSERVATION COMMITTEE Checklist of fish and mvertebrates Usted in the CITES appendices JNCC REPORT (SSN0963-«OStl JOINT NATURE CONSERVATION COMMITTEE Report distribution Report Number: No. 238 Contract Number/JNCC project number: F7 1-12-332 Date received: 9 June 1995 Report tide: Checklist of fish and invertebrates listed in the CITES appendices Contract tide: Revised Checklists of CITES species database Contractor: World Conservation Monitoring Centre 219 Huntingdon Road, Cambridge, CB3 ODL Comments: A further fish and invertebrate edition in the Checklist series begun by NCC in 1979, revised and brought up to date with current CITES listings Restrictions: Distribution: JNCC report collection 2 copies Nature Conservancy Council for England, HQ, Library 1 copy Scottish Natural Heritage, HQ, Library 1 copy Countryside Council for Wales, HQ, Library 1 copy A T Smail, Copyright Libraries Agent, 100 Euston Road, London, NWl 2HQ 5 copies British Library, Legal Deposit Office, Boston Spa, Wetherby, West Yorkshire, LS23 7BQ 1 copy Chadwick-Healey Ltd, Cambridge Place, Cambridge, CB2 INR 1 copy BIOSIS UK, Garforth House, 54 Michlegate, York, YOl ILF 1 copy CITES Management and Scientific Authorities of EC Member States total 30 copies CITES Authorities, UK Dependencies total 13 copies CITES Secretariat 5 copies CITES Animals Committee chairman 1 copy European Commission DG Xl/D/2 1 copy World Conservation Monitoring Centre 20 copies TRAFFIC International 5 copies Animal Quarantine Station, Heathrow 1 copy Department of the Environment (GWD) 5 copies Foreign & Commonwealth Office (ESED) 1 copy HM Customs & Excise 3 copies M Bradley Taylor (ACPO) 1 copy ^\(\\ Joint Nature Conservation Committee Report No.
    [Show full text]
  • Shrinking Shark Numbers on the Great Barrier Reef Unlikely to Have Cascading Impacts
    Khaled bin Sultan Living Oceans Foundation 821 Chesapeake Avenue #3568 • Annapolis, MD 21403 443.221.6844 • LivingOceansFoundation.org FOR IMMEDIATE RELEASE Shrinking shark numbers on the Great Barrier Reef unlikely to have cascading impacts New evidence suggests that reef sharks exert weak control over coral reef food webs Shark populations are dwindling worldwide, and scientists are concerned that the decline could trigger a cascade of impacts that hurt coral reefs. But a new paper published in Ecology suggests that the effects of shark losses are unlikely to reverberate throughout the marine food web. Instead, the findings point to physical and ecological features, like the structure of coral reefs and patterns of water movement, as important regulators of coral reef communities. Lead author Amelia Desbiens, a marine ecologist at the University of Queensland in Brisbane, Australia, conducted the study using data collected by the Khaled bin Sultan Living Oceans Foundation during its 2014 Global Reef Expedition, which surveyed shark populations on the northern Great Barrier Reef. Back then, this area was one of the most pristine reef regions in the world. The divers were heartened by the dizzying array of fish species in some locations, counting a total of 433 species of coral reef fish across their study area. “We were pleasantly surprised at the status of the coral reefs and fish communities in the northern Great Barrier Reef when we surveyed them in 2014,” said Alex Dempsey, Director of Science Management at the Khaled bin Sultan Living Oceans Foundation, and one of the paper’s authors. “We saw a relatively high percentage of live coral cover, and an abundance of reef fish species that gave us hope that perhaps these reef systems were resilient and have been able to persistently flourish.” They also found that no-fishing zones had four times as many reef sharks as the zones that allow fishing.
    [Show full text]
  • Florida Keys…
    What Do We Know? • Florida Keys… − Stony coral benthic cover declined by 40% from 1996 – 2009 (Ruzicka et al. 2013). − Potential Driving Factor? Stress due to extreme cold & warm water temperatures − Stony coral communities in patch reefs remained relatively constant after the 1998 El Niño (Ruzicka et al. 2013). − Patch reefs exposed to moderate SST Carysfort Reef - Images from Gene Shinn - USGS Photo Gallery variability exhibited the highest % live coral cover (Soto et al. 2011). Objective To test if the differences in stony coral diversity on Florida Keys reefs were correlated with habitats or SST variability from 1996 - 2010. Methods: Coral Reef Evaluation & Monitoring Program (CREMP) % coral cover 43 species DRY TORTUGAS UPPER KEYS MIDDLE KEYS LOWER KEYS 36 CREMP STATIONS (Patch Reefs (11), Offshore Shallow (12), Offshore Deep (13)) Methods: Sea Surface Temperature (SST) • Annual SST variance were derived from weekly means. • Categories for SST variability (variance): • Low (<7.0°C2) • Intermediate (7.0 - 10.9°C2) • High (≥11.0°C2) Advanced Very High Resolution Radiometer (AVHRR) SST data Vega-Rodriguez M et al. (2015) Results 1 I 0.5 Acropora palmata I s i Millepora complanata x Multivariate Statistics A l a Acropora c i Agaricia agaricites n o Pseudodiploriarevealed clivosa cervicornisthat stonycomplex n a C 0 Porites astreoides Madracis auretenra h t i coral diversity varied w Diploria labyrinthiformis Agaricia lamarcki n o Siderastrea radians i t Porites porites a l e significantly with r r Orbicella annularis o C -0.5 Pseudodiploriahabitats strigosa Colpophyllia natansStephanocoenia intercepta Montastraea cavernosa Siderastrea siderea Canonical Analysis of Principal Coordinates (CAP) -1 0.6 -1 -0.5 0 0.5 1 Correlation with Canonical Axis I ) % 0.4 7 6 .
    [Show full text]
  • Impact of the 2005 Coral Bleaching Event on Porites Porites and Colpophyllia Natans at Tektite Reef, US Virgin Islands
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Springer - Publisher Connector Coral Reefs (2007) 26:689–693 DOI 10.1007/s00338-007-0241-y NOTE Impact of the 2005 coral bleaching event on Porites porites and Colpophyllia natans at Tektite Reef, US Virgin Islands K. R. T. Whelan · J. Miller · O. Sanchez · M. Patterson Received: 7 August 2006 / Accepted: 19 April 2007 / Published online: 6 June 2007 © Springer-Verlag 2007 Abstract A thermal stress anomaly in 2005 caused mass Introduction coral bleaching at a number of north-east Caribbean reefs. The impact of the thermal stress event and subsequent Coral bleaching occurs when coral polyps loose pigment or White-plague disease type II on Porites porites and Colpo- expel zooxanthellae due to physiological stress, which phyllia natans was monitored using a time series of photo- recently has been most-often related to high water tempera- graphs from Tektite Reef, Virgin Islands National Park, tures and high solar radiation (Brown 1997; Winter et al. St. John. Over 92% of the P. porites and 96% of the 1998; Santavy et al. 2005). Since the 1980s, reports of coral C. natans experienced extensive bleaching (>30% of col- bleaching in the Caribbean have increased, with major ony bleached). During the study, 56% of P. porites and Caribbean-wide bleaching occurring in 1997–1998 (Hoegh- 42% of C. natans experienced whole-colony mortality Guldberg 1999; Aronson et al. 2000; Gardner et al. 2003). within the sample plots. While all whole-colony mortality Approximately 43–47% of coral tissue bleached at two St of P.
    [Show full text]
  • Review on Hard Coral Recruitment (Cnidaria: Scleractinia) in Colombia
    Universitas Scientiarum, 2011, Vol. 16 N° 3: 200-218 Disponible en línea en: www.javeriana.edu.co/universitas_scientiarum 2011, Vol. 16 N° 3: 200-218 SICI: 2027-1352(201109/12)16:3<200:RHCRCSIC>2.0.TS;2-W Invited review Review on hard coral recruitment (Cnidaria: Scleractinia) in Colombia Alberto Acosta1, Luisa F. Dueñas2, Valeria Pizarro3 1 Unidad de Ecología y Sistemática, Departamento de Biología, Facultad de Ciencias, Pontificia Universidad Javeriana, Bogotá, D.C., Colombia. 2 Laboratorio de Biología Molecular Marina - BIOMMAR, Departamento de Ciencias Biológicas, Facultad de Ciencias, Universidad de los Andes, Bogotá, D.C., Colombia. 3 Programa de Biología Marina, Facultad de Ciencias Naturales, Universidad Jorge Tadeo Lozano. Santa Marta. Colombia. * [email protected] Recibido: 28-02-2011; Aceptado: 11-05-2011 Abstract Recruitment, defined and measured as the incorporation of new individuals (i.e. coral juveniles) into a population, is a fundamental process for ecologists, evolutionists and conservationists due to its direct effect on population structure and function. Because most coral populations are self-feeding, a breakdown in recruitment would lead to local extinction. Recruitment indirectly affects both renewal and maintenance of existing and future coral communities, coral reef biodiversity (bottom-up effect) and therefore coral reef resilience. This process has been used as an indirect measure of individual reproductive success (fitness) and is the final stage of larval dispersal leading to population connectivity. As a result, recruitment has been proposed as an indicator of coral-reef health in marine protected areas, as well as a central aspect of the decision-making process concerning management and conservation.
    [Show full text]
  • SEDIMENTARY FRAMEWORK of Lmainland FRINGING REEF DEVELOPMENT, CAPE TRIBULATION AREA
    GREAT BARRIER REEF MARINE PARK AUTHORITY TECHNICAL MEMORANDUM GBRMPA-TM-14 SEDIMENTARY FRAMEWORK OF lMAINLAND FRINGING REEF DEVELOPMENT, CAPE TRIBULATION AREA D.P. JOHNSON and RM.CARTER Department of Geology James Cook University of North Queensland Townsville, Q 4811, Australia DATE November, 1987 SUMMARY Mainland fringing reefs with a diverse coral fauna have developed in the Cape Tribulation area primarily upon coastal sedi- ment bodies such as beach shoals and creek mouth bars. Growth on steep rocky headlands is minor. The reefs have exten- sive sandy beaches to landward, and an irregular outer margin. Typically there is a raised platform of dead nef along the outer edge of the reef, and dead coral columns lie buried under the reef flat. Live coral growth is restricted to the outer reef slope. Seaward of the reefs is a narrow wedge of muddy, terrigenous sediment, which thins offshore. Beach, reef and inner shelf sediments all contain 50% terrigenous material, indicating the reefs have always grown under conditions of heavy terrigenous influx. The relatively shallow lower limit of coral growth (ca 6m below ADD) is typical of reef growth in turbid waters, where decreased light levels inhibit coral growth. Radiocarbon dating of material from surveyed sites confirms the age of the fossil coral columns as 33304110 ybp, indicating that they grew during the late postglacial sea-level high (ca 5500-6500 ybp). The former thriving reef-flat was killed by a post-5500 ybp sea-level fall of ca 1 m. Although this study has not assessed the community structure of the fringing reefs, nor whether changes are presently occur- ring, it is clear the corals present today on the fore-reef slope have always lived under heavy terrigenous influence, and that the fossil reef-flat can be explained as due to the mid-Holocene fall in sea-level.
    [Show full text]
  • Fish Feeding and Dynamics of Soft-Sediment Mollusc Populations in a Coral Reef Lagoon
    MARINE ECOLOGY PROGRESS SERIES Published March 3 Mar. Ecol. Prog. Ser. Fish feeding and dynamics of soft-sediment mollusc populations in a coral reef lagoon G. P. Jones*, D. J. Ferrelle*,P. F. Sale*** School of Biological Sciences, University of Sydney, Sydney 2006, N.S.W., Australia ABSTRACT: Large coral reef fish were experimentally excluded from enclosed plots for 2 yr to examine their effect on the dynamics of soft sediment mollusc populations from areas in One Tree lagoon (Great Barrier Reef). Three teleost fish which feed on benthic molluscs. Lethrinus nebulosus, Diagramrna pictum and Pseudocaranx dentex, were common in the vicinity of the cages. Surveys of feeding scars in the sand indicated similar use of cage control and open control plots and effective exclusion by cages. The densities of 10 common species of prey were variable between locations and among times. Only 2 species exhibited an effect attributable to feeding by fish, and this was at one location only. The effect size was small relative to the spatial and temporal variation in numbers. The power of the test was sufficient to detect effects of fish on most species, had they occurred. A number of the molluscs exhibited annual cycles in abundance, with summer peaks due to an influx of juveniles but almost total loss of this cohort in winter. There was no evidence that predation altered the size-structure of these populations. While predation by fish is clearly intense, it does not have significant effects on the demo- graphy of these molluscs. The results cast doubt on the generality of the claim that predation is an important structuring agent in tropical communities.
    [Show full text]
  • 1 the Influence of Groyne Fields and Other Hard Defences on the Shoreline Configuration
    1 The Influence of Groyne Fields and Other Hard Defences on the Shoreline Configuration 2 of Soft Cliff Coastlines 3 4 Sally Brown1*, Max Barton1, Robert J Nicholls1 5 6 1. Faculty of Engineering and the Environment, University of Southampton, 7 University Road, Highfield, Southampton, UK. S017 1BJ. 8 9 * Sally Brown ([email protected], Telephone: +44(0)2380 594796). 10 11 Abstract: Building defences, such as groynes, on eroding soft cliff coastlines alters the 12 sediment budget, changing the shoreline configuration adjacent to defences. On the 13 down-drift side, the coastline is set-back. This is often believed to be caused by increased 14 erosion via the ‘terminal groyne effect’, resulting in rapid land loss. This paper examines 15 whether the terminal groyne effect always occurs down-drift post defence construction 16 (i.e. whether or not the retreat rate increases down-drift) through case study analysis. 17 18 Nine cases were analysed at Holderness and Christchurch Bay, England. Seven out of 19 nine sites experienced an increase in down-drift retreat rates. For the two remaining sites, 20 retreat rates remained constant after construction, probably as a sediment deficit already 21 existed prior to construction or as sediment movement was restricted further down-drift. 22 For these two sites, a set-back still evolved, leading to the erroneous perception that a 23 terminal groyne effect had developed. Additionally, seven of the nine sites developed a 24 set back up-drift of the initial groyne, leading to the defended sections of coast acting as 1 25 a hard headland, inhabiting long-shore drift.
    [Show full text]