The Deltaic Nature of Amazon Shelf Sedimentation

Total Page:16

File Type:pdf, Size:1020Kb

The Deltaic Nature of Amazon Shelf Sedimentation The deltaic nature of Amazon shelf sedimentation C. A. NITTROUER \ S. A. KUEHL* > Department of Marine, Earth and Atmospheric Sciences, North Carolina State University, Raleigh North Carolina 27695 D. J. DEMASTER J R. O. KOWSMANN CENPES/PETROBRAS, Rio de Janeiro, Cep. 21910, Brazü ABSTRACT deposits. This fine-scale stratification resem- mouth. Despite the supply of more than a billion bles deposits of (respectively) the distributary- tons of sediment each year, prograding subaerial Despite the annual discharge of more than mouth bar, distal bar, and prodelta observed deposits near the Amazon River mouth are a billion tons of sediment by the Amazon for the Mississippi and other deltas. much subdued relative to many other rivers. In River, the sedimentary environment near the The Amazon River has built a subaqueous fact, the physiographic expression at the Amazon river mouth has little subaerial expression feature which stretches for hundreds of River mouth closely resembles that of an estuary. and thus does not meet the classic definition kilometres offshore and alongshore from its This paper describes recent stratigraphic ob- of a delta. The river mouth, however, is not mouth. The feature is prograding seaward servations of the continental shelf at the mouth an estuary, eithei. These observations raise a and accreting upward, and it contains fine- of the Amazon River. Strata are evaluated on msyor question as to what type of sedimen- scale stratification typical of classic deltas. vertical scales ranging from tens of metres (seis- tary environment the Amazon river mouth The feature forming at the mouth of the mic stratigraphy) to millimetres (sedimentary represents. Amazon is a subaqueous delta; it differs from structures). The objectives are to examine strati- Seismic stratigraphy has been examined on classic deltas primarily in its lack of subaerial graphic relationships at the Amazon River the continental shelf at the mouth of the expression. Subaqueous deltas, such as the mouth, to compare them with sedimentation at Amazon River using high-frequency (3.5- Amazon, represent the general case of a other river mouths, and to consider deltaic kHz) seismic records from about 6,000 km of major river entering an energetic oceanic sedimentation in an environment with little sub- ship track. These records demonstrate three regime. aerial expression. regions. (1) <4l0-m water depth—topset strata composed primarily of muddy sediment INTRODUCTION BACKGROUND with sandy interlieds that dip gently and di- verge seaward; stratification (sandy inter- The geologic and economic importance of Deltaic Sedimentation beds) that becomes less predominant north- ancient deltaic deposits has led to extensive eval- westward along the dispersal system. (2) uation and synthesis of knowledge about modern Gilbert (1885) introduced the concept of -40- to ~60-m water depth—foreset strata that deltas (see, for example, van Straaten, 1964; delta progradation: relatively steeply dipping dip relatively steeply (but <1°) and converge Shirley and Ragsdale, 1966; Morgan, 1970; foreset deposits prograde outward over thi i, flat- seaward. (3) -6(1- to -100-m water depth— Broussard, 1975; American Assoc. Petroleum lying, finer-grained bottomset deposits; and bottomset strata ilhat form a thin, acoustically Geologists, 1976). Notably missing from these gently clipping topset deposits accrete upward transparent layer of mud, which is burying detailed presentations is the world's largest river, upon the foreset deposits. Gilbert (1885, 1890) sandy bedforms on the surface of a basal the Amazon River. The Amazon River mouth is studied Pleistocene lake deltas, and some signifi- (transgressive) sand layer. The large-scale discussed in the literature both as a delta cant differences exist between these delUis and structure which the deposits of these regions (Wright, 1978) and as an estuary (Friedman modern ocean deltas, which generally contain create is a sigmoidal clinoform. Fine-scale and Sanders, 1978); however, its sedimentary finer sediment and more gentle foreset slopes. sedimentary structures have been examined nature has not been documented sufficiently for The Mississippi delta has become the type ex- from the inner continental shelf using X- accurate appraisal. ample of modern deltas, and use of Gilbert's radiographs of about 140 cores (box cores The early Greeks used the word "delta" to topset-foreset-bottomset terminology has. been and large gravity cores). These X-radio- describe the shape of subaerial deposits at the replaced by a new classification of sedimentary graphs reveal: (1) physically stratified sand mouth of the Nile River. The first scientific study environments which is more compatible with near the river-mouth bar, (2) interbedded of delta stratification included subaerial deposits observations of the Mississippi delta (Coleman, mud and sand (in the shelf adjacent to the (topset) as a requisite to deltaic sequences (Gil- 1976; Wright, 1978). Distributaries crcss the river mouth, and (3) faintly laminated and bert, 188S). The first geological definition of a subaerial deltaic plain, and at their mouths is mottled mud surrounding the interbedded "delta" (Barrell, 1912, p. 381) described it as "a found the delta front, consisting of distributary- deposit partly subaerial built by a river into or mouth bar deposits and distal bar deposits. The against a body of permanent water." These asso- delta fiont has the greatest relief of the delta, but •Present address: Department of Geology, Univer- even so, the slopes for the delta front of the sity of South Carolina, Columbia, South Carolina ciations of subaerial features within a delta help 29208. to explain the confusion about the Amazon river Mississippi are less than 1°. The deposits of the Geological Society of America Bulletin, v. 97, p. 444-458,18 figs., April 1986. 444 Downloaded from http://pubs.geoscienceworld.org/gsa/gsabulletin/article-pdf/97/4/444/3445127/i0016-7606-97-4-444.pdf by guest on 25 September 2021 30' 50° 30' 49° Figure 1. Bathymétrie chart for the mouth of the Amazon River (modified from chart 200, Brazilian Directorate of Hydrography and Navigation). Hachured area represents broad transverse bar across the river mouth. Locations are shown for cores presented in this paper. Downloaded from http://pubs.geoscienceworld.org/gsa/gsabulletin/article-pdf/97/4/444/3445127/i0016-7606-97-4-444.pdf by guest on 25 September 2021 446 NITTROUER AND OTHERS distributary-mouth bar consist largely of the iment, resulting in faulting, slumping, and mud also should affect the subaqueous structure of bedload of the river and form physically strati- flowage (Coleman and others, 1974). Decay of deltas. fied sands. The suspended load accumulates in organic matter in the seabed can cause produc- the deeper and more quiescent region of the dis- tion of methane gas. The presence of such gas Sedimentation near the Amazon River Mouth tal bar, forming deposits of mud interlaminated usually is recognized by disruption of the seismic with sand. Beyond the delta front, there are pro- record and can lead to instability in the seabed The annual discharge of Amazon River water delta deposits, where the remaining silt and clay (Coleman, 1976). represents one-fifth of the world total for river accumulate as horizontally laminated deposits. Where the potential for delta formation exists, discharge, and it is more than an order of magni- Because of reduced accumulation rate, these the large-scale morphology of a delta is con- tude larger than that of the Mississippi River deposits can become mottled and homogenized trolled by several fluvial and oceanographic fac- (Gibbs, 1967). The difference between seasonal by bioturbation (Moore and Scruton, 1957). The tors (Coleman, 1976; Wright, 1978). The high flow and low flow of the Amazon is only a above sedimentary environments, with associ- amount and grain size of sediment discharged by factor of about two (Oltman, 1968). Because of ated sedimentary structures, commonly occur in a river affect estuarine infilling and delta pro- the large, continuous discharge, ocean water other deltas (for example, Niger delta; Allen, gradation. The nature of the fluvial jet entering never enters the Amazon River mouth ( Gibbs, 1965,1970). The seaward transition of environ- the ocean influences the dispersal of deltaic sed- 1970). On the adjacent continental shelf, the ments exhibits a progressive fining (Scruton, iments (Bates, 1953; Wright, 1977). The pri- fluvial discharge becomes a hypopycnal jet, and 1960). Delta projjradation causes the deposits to mary oceanographic processes affecting deltaic low-salinity water is transported hundreds of be superimpose^ which leads to upward configuration are surface waves and tidal cur- kilometres as a surface plume (Gibbs, 1970; coarsening. For many deltas, the basal (pro- rents (Wright and Coleman, 1973; Galloway, Curtin, 1983). The annual sediment discharge of delta) muds are not competent to bear the 1975). In some situations, coastal (shelf) cur- the Amazon is about 1.2 x 109 tons (Meade and weight of the overlying deposits, and the mud is rents also have a significant effect on dispersal of others, 1985), ranking it second in the world forced upward us diapiric intrusions (Nota, deltaic sediments (Murray and others, 1980). (Milliman and Meade, 1983). About 85% to 1958; Morgan and others, 1968; Shepard and The studies examining the impact of the above 95% of sediment discharged by the Amiizon is others, 1968). The rapid deposition of deltaic factors have focused on effects to the large-scale mud (silt and clay) (Gibbs, 1967; Meade, 1985), deposits can lead also to failures of surficial sed- subaerial morphology of deltas, but these factors and most sediment is injected to the ocean in suspension (Gibbs, 1976). 52°w Oceanographic processes affecting the disper- sal of Amazon sediment include strong ticlal and coastal currents as well as moderate surface waves. The tidal range near the river mouth commonly exceeds 6 m (NOAA, 1982), and tidal currents exceeding 100 cm/s have been measured on the shelf (near the river mouth) a couple of metres above the seabed (Curtin, 1983).
Recommended publications
  • Snohomish Estuary Wetland Integration Plan
    Snohomish Estuary Wetland Integration Plan April 1997 City of Everett Environmental Protection Agency Puget Sound Water Quality Authority Washington State Department of Ecology Snohomish Estuary Wetlands Integration Plan April 1997 Prepared by: City of Everett Department of Planning and Community Development Paul Roberts, Director Project Team City of Everett Department of Planning and Community Development Stephen Stanley, Project Manager Roland Behee, Geographic Information System Analyst Becky Herbig, Wildlife Biologist Dave Koenig, Manager, Long Range Planning and Community Development Bob Landles, Manager, Land Use Planning Jan Meston, Plan Production Washington State Department of Ecology Tom Hruby, Wetland Ecologist Rick Huey, Environmental Scientist Joanne Polayes-Wien, Environmental Scientist Gail Colburn, Environmental Scientist Environmental Protection Agency, Region 10 Duane Karna, Fisheries Biologist Linda Storm, Environmental Protection Specialist Funded by EPA Grant Agreement No. G9400112 Between the Washington State Department of Ecology and the City of Everett EPA Grant Agreement No. 05/94/PSEPA Between Department of Ecology and Puget Sound Water Quality Authority Cover Photo: South Spencer Island - Joanne Polayes Wien Acknowledgments The development of the Snohomish Estuary Wetland Integration Plan would not have been possible without an unusual level of support and cooperation between resource agencies and local governments. Due to the foresight of many individuals, this process became a partnership in which jurisdictional politics were set aside so that true land use planning based on the ecosystem rather than political boundaries could take place. We are grateful to the Environmental Protection Agency (EPA), Department of Ecology (DOE) and Puget Sound Water Quality Authority for funding this planning effort, and to Linda Storm of the EPA and Lynn Beaton (formerly of DOE) for their guidance and encouragement during the grant application process and development of the Wetland Integration Plan.
    [Show full text]
  • Elkhorn Slough Estuary
    A RICH NATURAL RESOURCE YOU CAN HELP! Elkhorn Slough Estuary WATER QUALITY REPORT CARD Located on Monterey Bay, Elkhorn Slough and surround- There are several ways we can all help improve water 2015 ing wetlands comprise a network of estuarine habitats that quality in our communities: include salt and brackish marshes, mudflats, and tidal • Limit the use of fertilizers in your garden. channels. • Maintain septic systems to avoid leakages. • Dispose of pharmaceuticals properly, and prevent Estuarine wetlands harsh soaps and other contaminants from running are rare in California, into storm drains. and provide important • Buy produce from local farmers applying habitat for many spe- sustainable management practices. cies. Elkhorn Slough • Vote for the environment by supporting candidates provides special refuge and bills favoring clean water and habitat for a large number of restoration. sea otters, which rest, • Let your elected representatives and district forage and raise pups officials know you care about water quality in in the shallow waters, Elkhorn Slough and support efforts to reduce question: How is the water in Elkhorn Slough? and nap on the salt marshes. Migratory shorebirds by the polluted run-off and to restore wetlands. thousands stop here to rest and feed on tiny creatures in • Attend meetings of the Central Coast Regional answer: It could be a lot better… the mud. Leopard sharks by the hundreds come into the Water Quality Control Board to share your estuary to give birth. concerns and support for action. Elkhorn Slough estuary hosts diverse wetland habitats, wildlife and recreational activities. Such diversity depends Thousands of people come to Elkhorn Slough each year JOIN OUR EFFORT! to a great extent on the quality of the water.
    [Show full text]
  • PESHTIGO RIVER DELTA Property Owner
    NORTHEAST - 10 PESHTIGO RIVER DELTA WETLAND TYPES Drew Feldkirchner Floodplain forest, lowland hardwood, swamp, sedge meadow, marsh, shrub carr ECOLOGY & SIGNIFICANCE supports cordgrass, marsh fern, sensitive fern, northern tickseed sunflower, spotted joe-pye weed, orange This Wetland Gem site comprises a very large coastal • jewelweed, turtlehead, marsh cinquefoil, blue skullcap wetland complex along the northwest shore of Green Bay and marsh bellflower. Shrub carr habitat is dominated three miles southeast of the city of Peshtigo. The wetland by slender willow; other shrub species include alder, complex extends upstream along the Peshtigo River for MARINETTE COUNTY red osier dogwood and white meadowsweet. Floodplain two miles from its mouth. This site is significant because forest habitats are dominated by silver maple and green of its size, the diversity of wetland community types ash. Wetlands of the Peshtigo River Delta support several present, and the overall good condition of the vegetation. - rare plant species including few-flowered spikerush, The complexity of the site – including abandoned oxbow variegated horsetail and northern wild raisin. lakes and a series of sloughs and lagoons within the river delta – offers excellent habitat for waterfowl. A number This Wetland Gem provides extensive, diverse and high of rare animals and plants have been documented using quality wetland habitat for many species of waterfowl, these wetlands. The area supports a variety of recreational herons, gulls, terns and shorebirds and is an important uses, such as hunting, fishing, trapping and boating. The staging, nesting and stopover site for many migratory Peshtigo River Delta has been described as the most birds. Rare and interesting bird species documented at diverse and least disturbed wetland complex on the west the site include red-shouldered hawk, black tern, yellow shore of Green Bay.
    [Show full text]
  • Delaware Bay Estuary Project Supporting the Conservation and Restoration Of
    U.S. Fish & Wildlife Service – Coastal Program Delaware Bay Estuary Project Supporting the conservation and restoration of the salt marshes of Delaware Bay People have altered the expansive salt marshes of Delaware Bay for centuries to farm salt hay, try to control mosquitoes, create channels for boats, to increase developable land, and other reasons all resulting in restricted tidal flow, disrupted sediment balances, or increasing erosion. Sea level rise and coastal storms threaten to further negatively impact the integrity of these salt marshes. As we alter or lose the marshes we lose the valuable habitats and ecological services they provide. tidal creek - Katherine Whittemore Addressing the all-important sediment balance of salt marshes is critical for preserving their resilience. A healthy resilient marsh may be able to keep pace with erosion and sea level rise through sediment accretion and growth Downe Twsp, NJ - Brian Marsh of vegetation. However, the delicate sediment balance of salt marshes is DBEP works to support efforts to learn more about the techniques often disrupted by barriers to tidal influence and altered drainage onto and to conserve and restore salt marshes and support the populations of fish and wildlife that rely on them. We support new and off the marsh resulting in sediment ongoing coastal resiliency initiatives and coastal planning as they starved systems, excessive mudflats, or pertain to habitat restoration and conservation. We are interested increased erosion. in finding effective tools and mechanisms for conserving and restoring salt marsh integrity on a meaningful scale and support efforts that bring partners together to approach this challenge.
    [Show full text]
  • Field Studies and 3D Modelling of Morphodynamics in a Meandering River Reach Dominated by Tides and Suspended Load
    fluids Article Field Studies and 3D Modelling of Morphodynamics in a Meandering River Reach Dominated by Tides and Suspended Load Qiancheng Xie 1,* , James Yang 2,3 and T. Staffan Lundström 1 1 Division of Fluid and Experimental Mechanics, Luleå University of Technology, 97187 Luleå, Sweden; [email protected] 2 Vattenfall AB, Research and Development, Hydraulic Laboratory, 81426 Älvkarleby, Sweden; [email protected] 3 Resources, Energy and Infrastructure, Royal Institute of Technology, 10044 Stockholm, Sweden * Correspondence: [email protected]; Tel.: +4672-2870-381 Received: 9 December 2018; Accepted: 20 January 2019; Published: 22 January 2019 Abstract: Meandering is a common feature in natural alluvial streams. This study deals with alluvial behaviors of a meander reach subjected to both fresh-water flow and strong tides from the coast. Field measurements are carried out to obtain flow and sediment data. Approximately 95% of the sediment in the river is suspended load of silt and clay. The results indicate that, due to the tidal currents, the flow velocity and sediment concentration are always out of phase with each other. The cross-sectional asymmetry and bi-directional flow result in higher sediment concentration along inner banks than along outer banks of the main stream. For a given location, the near-bed concentration is 2−5 times the surface value. Based on Froude number, a sediment carrying capacity formula is derived for the flood and ebb tides. The tidal flow stirs the sediment and modifies its concentration and transport. A 3D hydrodynamic model of flow and suspended sediment transport is established to compute the flow patterns and morphology changes.
    [Show full text]
  • A Synthesis of Information I
    Outer Continental Shelf Environmental Assessment Program * A Synthesis of Information I U.S. DEPARTMENT OF COMMERCE U.S. DEPARTMENT OF THE INTEXIOR National Oceanic and Atmospheric Administration Minerals Management Service National Ocean Service Alaska OCS Region Office of Oceanography and Marine Assessment . .:.% y! Ocean Assessments Division ' t. CU ' k Alaska Office OCS Study, MMS 89-0081 . '.'Y. 4 3 --- NOTICES This report has been prepared as part of the U.S. Department bf Commerce, National Oceanic and Atmospheric Administration's Outer Continental Shelf Environmental Assessment Program, and approved for publication. The inter- pretation of data and opinions expressed in this document are those of the authors. Approval does not necessarily signify that the contents reflect the views and policies of the Department of Commerce or those of the Department of the Interior. The National Oceanic and Atmospheric Administration (NOAA) does not approve, recommend, or endorse any proprietary material mentioned in this publication. No reference shall be made to NOAA or to this publication in any advertising or sales promotion which would indicate or imply that NOAA approves, recommends, or endorses any proprietary product or proprietary material mentioned herein, or which has as its purpose or intent to cause directly or indirectly the advertised product to be used or purchased because of this publication. Cover: LandsatTMimage of the Yukon Delta taken on Julg 22, 1975, showing the thamal gradients resulting from Yukon River discharge. In this image land is dqicted in sesof red indicating warmer temperatures versus the dark blues (colder temperatures) of Bering Sea waters. Yukon River water, cooh than the surround- ing land but wanner than marine waters, is represented bg a light aqua blue.
    [Show full text]
  • CLASSIFICATION of CALIFORNIA ESTUARIES BASED on NATURAL CLOSURE PATTERNS: TEMPLATES for RESTORATION and MANAGEMENT Revised
    CLASSIFICATION OF CALIFORNIA ESTUARIES BASED ON NATURAL CLOSURE PATTERNS: TEMPLATES FOR RESTORATION AND MANAGEMENT Revised David K. Jacobs Eric D. Stein Travis Longcore Technical Report 619.a - August 2011 Classification of California Estuaries Based on Natural Closure Patterns: Templates for Restoration and Management David K. Jacobs1, Eric D. Stein2, and Travis Longcore3 1UCLA Department of Ecology and Evolutionary Biology 2Southern California Coastal Water Research Project 3University of Southern California - Spatial Sciences Institute August 2010 Revised August 2011 Technical Report 619.a ABSTRACT Determining the appropriate design template is critical to coastal wetland restoration. In seasonally wet and semi-arid regions of the world coastal wetlands tend to close off from the sea seasonally or episodically, and decisions regarding estuarine mouth closure have far reaching implications for cost, management, and ultimate success of coastal wetland restoration. In the past restoration planners relied on an incomplete understanding of the factors that influence estuarine mouth closure. Consequently, templates from other climatic/physiographic regions are often inappropriately applied. The first step to addressing this issue is to develop a classification system based on an understanding of the processes that formed the estuaries and thus define their pre-development structure. Here we propose a new classification system for California estuaries based on the geomorphic history and the dominant physical processes that govern the formation of the estuary space or volume. It is distinct from previous estuary closure models, which focused primarily on the relationship between estuary size and tidal prism in constraining closure. This classification system uses geologic origin, exposure to littoral process, watershed size and runoff characteristics as the basis of a conceptual model that predicts likely frequency and duration of closure of the estuary mouth.
    [Show full text]
  • Estuarine Wetlands
    ESTUARINE WETLANDS • An estuary occurs where a river meets the sea. • Wetlands connected with this environment are known as estuarine wetlands. • The water has a mix of the saltwater tides coming in from the ocean and the freshwater from the river. • They include tidal marshes, salt marshes, mangrove swamps, river deltas and mudflats. • They are very important for birds, fish, crabs, mammals, insects. • They provide important nursery grounds, breeding habitat and a productive food supply. • They provide nursery habitat for many species of fish that are critical to Australia’s commercial and recreational fishing industries. • They provide summer habitat for migratory wading birds as they travel between the northern and southern hemispheres. Estuarine wetlands in Australia Did you know? Kakadu National Park, Northern Territory: Jabiru build large, two-metre wide • Kakadu has four large river systems, the platform nests high in trees. The East, West and South Alligator rivers nests are made up of sticks, branches and the Wildman river. Most of Kakadu’s and lined with rushes, water-plants wetlands are a freshwater system, but there and mud. are many estuarine wetlands around the mouths of these rivers and other seasonal creeks. Moreton Bay, Queensland: • Kakadu is famous for the large numbers of birds present in its wetlands in the dry • Moreton Bay has significant mangrove season. habitat. • Many wetlands in Kakadu have a large • The estuary supports fish, birds and other population of saltwater crocodiles. wildlife for feeding and breeding. • Seagrasses in Moreton Bay provide food and habitat for dugong, turtles, fish and crustaceans. www.environment.gov.au/wetlands Plants and animals • Saltwater crocodiles live in estuarine and • Dugongs, which are also known as sea freshwater wetlands of northern Australia.
    [Show full text]
  • Estuary Bird Cards
    TEACHER MASTER Estuary Bird Cards Great Blue Heron Osprey Willet Roseate Spoonbill Great Egret Glossy Ibis Marsh Wren Tern Brown Pelican Whooping Crane Sandpiper Avocet Woodstork Snowy Egret Black Skimmer Crested Comorant Activity 9: Bountiful Birds 10 TEACHER MASTER Estuary Habitats Salt marsh Mangrove swamp Mudflats Lagoon low tide Seagrass beds Activity 9: Bountiful Birds 11 STUDENT MASTER Great Birds of the Estuaries Estuaries actually contain a number of different habitats, each better or worse suited for different species of birds, as well as other estuary animals and plants. Here are five of the main estuary habitats: 1. A lagoon is an area of shallow, open water, separated from the open ocean by some sort of barrier, such as a barrier island. The water in a lagoon can either be as salty as the ocean or brackish. 2. A salt marsh has non-tree plants (grasses, shrubs, etc.) whose roots grow in soil acted upon by tides, but the plants are mostly never submerged. 3. The woody trees that grow in a mangrove swamp grow in soil affected by tides. Mangrove trees only grow in estuaries that never freeze. 4. Seagrass beds are always submerged underwater. Seagrass is photosynthetic, so it grows in water that is shallow and clear enough for the grass to get sunlight. Seagrass is anchored to the muddy or sandy bottom. 5. Mudflats are sometimes also called tidal flats. They are broad, flat areas of extremely fine sediment (mud) that become exposed at low tide. There are other estuary habitats. A beach or rocky shore can be part of the estuary.
    [Show full text]
  • Analyzing Trends of Dike-Ponds Between 1978 and 2016 Using Multi-Source Remote Sensing Images in Shunde District of South China
    sustainability Article Analyzing Trends of Dike-Ponds between 1978 and 2016 Using Multi-Source Remote Sensing Images in Shunde District of South China Fengshou Li 1, Kai Liu 1,* , Huanli Tang 2, Lin Liu 3,4,* and Hongxing Liu 4,5 1 Guangdong Key Laboratory for Urbanization and Geo-simulation, Guangdong Provincial Engineering Research Center for Public Security and Disaster, School of Geography and Planning, Sun Yat-Sen University, Guangzhou 510275, China; [email protected] 2 Guangzhou Zengcheng District Urban and Rural Planning and Surveying and Mapping Geographic Information Institute, Guangzhou 511300, China; [email protected] 3 Center of Geo-Informatics for Public Security, School of Geographic Sciences, Guangzhou University, Guangzhou 510006, China 4 Department of Geography and Geographic Information Science, University of Cincinnati, Cincinnati, OH 45221, USA; [email protected] 5 Department of Geography, the University of Alabama, Tuscaloosa, AL 35487, USA * Correspondence: [email protected] (K.L.); [email protected] (L.L.); Tel.: +86-020-8411-3044 (K.L.); +1-513-556-3429 (L.L.); Fax: +86-020-8411-3057 (K.L. & L.L.) Received: 27 August 2018; Accepted: 26 September 2018; Published: 30 September 2018 Abstract: Dike-ponds have experienced significant changes in the Pearl River Delta region over the past several decades, especially since China’s economic reform, which has seriously affected the construction of ecological environments. In order to monitor the evolution of dike-ponds, in this study we use multi-source remote sensing images from 1978 to 2016 to extract dike-ponds in several periods using the nearest neighbor classification method.
    [Show full text]
  • Dispersal of Larval Suckers at the Williamson River Delta, Upper Klamath Lake, Oregon, 2006–09
    Prepared in cooperation with the Bureau of Reclamation Dispersal of Larval Suckers at the Williamson River Delta, Upper Klamath Lake, Oregon, 2006–09 Scientific Investigations Report 2012–5016 U.S. Department of the Interior U.S. Geological Survey Cover: Inset: Larval sucker from Upper Klamath Lake, Oregon. (Photograph taken by Allison Estergard, Student, Oregon State University, Corvallis, Oregon, 2011.) Top: Photograph taken from the air of the flooded Williamson River Delta, Upper Klamath Lake, Oregon. (Photograph taken by Charles Erdman, Fisheries Technician, Williamson River Delta Preserve, Klamath Falls, Oregon, 2008.) Bottom left: Photograph of a pop net used by The Nature Conservancy to collect larval suckers in Upper Klamath Lake and the Williamson River Delta, Oregon. (Photograph taken by Heather Hendrixson, Director, Williamson River Delta Preserve, Klamath Falls, Oregon, 2006.) Bottom middle: Photograph of a larval trawl used by Oregon State University to collect larval suckers in Upper Klamath Lake and the Williamson River Delta, Oregon. (Photograph taken by David Simon, Senior Faculty Research Assistant, Oregon State University, Corvallis, Oregon, 2010.) Bottom right: Photograph of a plankton net used by the U.S. Geological Survey to collect larval suckers in Upper Klamath Lake and the Williamson River Delta, Oregon. (Photographer unknown, Klamath Falls, Oregon, 2009.) Dispersal of Larval Suckers at the Williamson River Delta, Upper Klamath Lake, Oregon, 2006–09 By Tamara M. Wood, U.S. Geological Survey, Heather A. Hendrixson, The Nature Conservancy, Douglas F. Markle, Oregon State University, Charles S. Erdman, The Nature Conservancy, Summer M. Burdick, U.S. Geological Survey, Craig M. Ellsworth, U.S. Geological Survey, and Norman L.
    [Show full text]
  • The Economics of Dead Zones: Causes, Impacts, Policy Challenges, and a Model of the Gulf of Mexico Hypoxic Zone S
    58 The Economics of Dead Zones: Causes, Impacts, Policy Challenges, and a Model of the Gulf of Mexico Hypoxic Zone S. S. Rabotyagov*, C. L. Klingy, P. W. Gassmanz, N. N. Rabalais§ ô and R. E. Turner Downloaded from Introduction The BP Deepwater Horizon oil spill in the Gulf of Mexico in 2010 increased public awareness and http://reep.oxfordjournals.org/ concern about long-term damage to ecosystems, and casual readers of the news headlines may have concluded that the spill and its aftermath represented the most significant and enduring environmental threat to the region. However, the region faces other equally challenging threats including the large seasonal hypoxic, or “dead,” zone that occurs annually off the coast of Louisiana and Texas. Even more concerning is the fact that such dead zones have been appearing worldwide at proliferating rates (Conley et al. 2011; Diaz and Rosenberg 2008). Nutrient over- enrichment is the main cause of these dead zones, and nutrient-fed hypoxia is now widely at Iowa State University on January 27, 2014 considered an important threat to the health of aquatic ecosystems (Doney 2010). The rather alarming term dead zone is surprisingly appropriate: hypoxic regions exhibit oxygen levels that are too low to support many aquatic organisms including commercially desirable species. While some dead zones are naturally occurring, their number, size, and *School of Environmental and Forest Sciences, University of Washington, Seattle, Washington, USA; e-mail: [email protected] yCenter for Agricultural and Rural Development,
    [Show full text]