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1

Hay, Mark. „Coastal Ecology“. Ecology 67, Nr. 5 (Oktober 1986): 1438. http://dx.doi.org/10.2307/1938708.

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2

Snedaker, Samuel C. „Tropical coastal ecology“. Environmental Biology of Fishes 42, Nr. 2 (Februar 1995): 215–17. http://dx.doi.org/10.1007/bf00002000.

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3

Lee Smee, Delbert. „Coastal Ecology: Living Shorelines Reduce Coastal Erosion“. Current Biology 29, Nr. 11 (Juni 2019): R411—R413. http://dx.doi.org/10.1016/j.cub.2019.04.044.

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4

Pittman, SJ, RT Kneib und CA Simenstad. „Practicing coastal seascape ecology“. Marine Ecology Progress Series 427 (12.04.2011): 187–90. http://dx.doi.org/10.3354/meps09139.

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5

Johnson, Ann F., W. G. Beeftink, J. Rozema und A. H. L. Huiskes. „Ecology of Coastal Vegetation.“ Bulletin of the Torrey Botanical Club 113, Nr. 2 (April 1986): 186. http://dx.doi.org/10.2307/2995948.

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6

Valiela, I., und S. E. Fox. „ECOLOGY: Managing Coastal Wetlands“. Science 319, Nr. 5861 (18.01.2008): 290–91. http://dx.doi.org/10.1126/science.1153477.

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7

Mann, K. H. „An introduction to coastal ecology“. Limnology and Oceanography 32, Nr. 4 (Juli 1987): 1015. http://dx.doi.org/10.4319/lo.1987.32.4.1015.

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8

Hughes, R. N., P. J. S. Boaden und R. Seed. „An Introduction to Coastal Ecology.“ Journal of Ecology 74, Nr. 3 (September 1986): 906. http://dx.doi.org/10.2307/2260408.

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9

Paskoff, Roland P. „Coastal dunes, ecology and conservation“. Journal of Coastal Conservation 9, Nr. 2 (2003): 190. http://dx.doi.org/10.1652/1400-0350(2003)009[0190:br]2.0.co;2.

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10

Gerkema, Theo, Catharina J. M. Philippart und Henk W. van der Veer. „North Sea coastal ecology: Preface“. Journal of Sea Research 127 (September 2017): 1. http://dx.doi.org/10.1016/j.seares.2017.06.016.

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11

Collins, Andrew E. „Vulnerability to coastal cholera ecology“. Social Science & Medicine 57, Nr. 8 (Oktober 2003): 1397–407. http://dx.doi.org/10.1016/s0277-9536(02)00519-1.

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12

McLachlan, Anton. „Ecology of coastal dune fauna“. Journal of Arid Environments 21, Nr. 2 (September 1991): 229–43. http://dx.doi.org/10.1016/s0140-1963(18)30684-0.

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13

Sutherland, John P. „Ecology of the Coastal Zone“. Ecology 71, Nr. 3 (Juni 1990): 1225. http://dx.doi.org/10.2307/1937398.

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14

Pringle, Ada W., Heather Viles und Tom Spencer. „Coastal Problems: Geomorphology, Ecology and Society at the Coast“. Geographical Journal 162, Nr. 2 (Juli 1996): 226. http://dx.doi.org/10.2307/3059890.

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15

Shepherd, Mike. „Coastal Problems: Geomorphology, Ecology and Society at the Coast“. New Zealand Geographer 53, Nr. 1 (April 1997): 55–56. http://dx.doi.org/10.1111/j.1745-7939.1997.tb00478.x.

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16

Kwak, Thomas J., Robert J. Naiman und Robert E. Bilby. „Pacific Coastal River Ecology and Management“. Ecology 81, Nr. 3 (März 2000): 882. http://dx.doi.org/10.2307/177387.

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17

Smardon, Richard. „COASTAL MARSHES: ECOLOGY AND WILDLIFE MANAGEMENT“. Landscape Journal 9, Nr. 1 (1990): 56–57. http://dx.doi.org/10.3368/lj.9.1.56.

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18

TAN, H. R. Skjoldal, C. Hopkins, K. E. Erikstad und H. P. Leinaas. „Ecology of Fjords and Coastal Waters“. Colonial Waterbirds 20, Nr. 2 (1997): 376. http://dx.doi.org/10.2307/1521711.

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19

Scarborough, Courtney, Zoë S. Welch, Jono Wilson, Mary G. Gleason, Vienna R. Saccomanno und Benjamin S. Halpern. „The historical ecology of coastal California“. Ocean & Coastal Management 230 (November 2022): 106352. http://dx.doi.org/10.1016/j.ocecoaman.2022.106352.

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20

Kwak, Thomas J. „Pacific Coastal River Ecology and Management“. Ecology 81, Nr. 3 (März 2000): 883–84. http://dx.doi.org/10.1890/0012-9658(2000)081[0883:pcream]2.0.co;2.

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21

Roe, Maggie. „Coastal Landscape Ecology: Involving the community“. Landscape Research 25, Nr. 3 (November 2000): 377–82. http://dx.doi.org/10.1080/713684678.

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22

Stillman, Richard A., und John D. Goss-Custard. „Individual-based ecology of coastal birds“. Biological Reviews 85, Nr. 3 (24.11.2009): 413–34. http://dx.doi.org/10.1111/j.1469-185x.2009.00106.x.

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23

Singh, Jai S. „Coastal Ecology: Development, Directions and Dimensions“. Maritime Affairs:Journal of the National Maritime Foundation of India 9, Nr. 1 (Juni 2013): 1–29. http://dx.doi.org/10.1080/09733159.2013.798106.

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24

Philippart, Catharina J. M., Theo Gerkema und Henk W. van der Veer. „North Sea coastal ecology: Future challenges“. Journal of Sea Research 127 (September 2017): 227–30. http://dx.doi.org/10.1016/j.seares.2017.07.004.

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25

Elliott, Michael. „Ecology of fjords and coastal waters“. Marine Pollution Bulletin 34, Nr. 6 (Juni 1997): 491–92. http://dx.doi.org/10.1016/s0025-326x(97)00033-7.

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26

Gilbert, M. E., N. W. Pammenter und B. S. Ripley. „New perspectives in coastal dune ecology“. South African Journal of Botany 74, Nr. 2 (April 2008): 367. http://dx.doi.org/10.1016/j.sajb.2008.01.057.

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27

Cressey, Daniel. „Gulf ecology hit by coastal development“. Nature 479, Nr. 7373 (November 2011): 277. http://dx.doi.org/10.1038/479277a.

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28

Uttieri, Marco, Ylenia Carotenuto, Iole Di Capua und Vittoria Roncalli. „Ecology of Marine Zooplankton“. Journal of Marine Science and Engineering 11, Nr. 10 (27.09.2023): 1875. http://dx.doi.org/10.3390/jmse11101875.

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29

Weisberg, Robert H. „Coastal Ocean Pollution, Water Quality, and Ecology“. Marine Technology Society Journal 45, Nr. 2 (01.03.2011): 35–42. http://dx.doi.org/10.4031/mtsj.45.2.1.

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30

Day, John W., A. Eleftheriou, A. Ansell und C. Smith. „Biology and Ecology of Shallow Coastal Waters“. Estuaries 20, Nr. 3 (September 1997): 656. http://dx.doi.org/10.2307/1352625.

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31

Lithgow, D., M. L. Martínez, J. B. Gallego-Fernández, P. A. Hesp, P. Flores, S. Gachuz, N. Rodríguez-Revelo, O. Jiménez-Orocio, G. Mendoza-González und L. L. Álvarez-Molina. „Linking restoration ecology with coastal dune restoration“. Geomorphology 199 (Oktober 2013): 214–24. http://dx.doi.org/10.1016/j.geomorph.2013.05.007.

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32

Stratford, Charlie, und Paul Rooney. „Special issue – coastal dune slack hydro-ecology“. Journal of Coastal Conservation 21, Nr. 5 (Oktober 2017): 573–76. http://dx.doi.org/10.1007/s11852-017-0559-8.

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33

Duran, Robert, Philippe Cuny, Patricia Bonin und Cristiana Cravo-Laureau. „Microbial ecology of hydrocarbon-polluted coastal sediments“. Environmental Science and Pollution Research 22, Nr. 20 (18.09.2015): 15195–99. http://dx.doi.org/10.1007/s11356-015-5373-y.

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34

Sommer, Bea. „Australian Saltmarsh Ecology“. Pacific Conservation Biology 16, Nr. 1 (2010): 71. http://dx.doi.org/10.1071/pc100071.

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Australia, including its territorial islands, is surrounded by almost 60 000 km of coastline (Geoscience Australia, http://www.ga.gov.au/education/) and, according to Saintilan, coastal saltmarshes occupy some 16 000 km2. Saltmarshes provide valuable ecosystem services and are generally recognized as among the most productive ecosystems on Earth. This is considered to be ecologically important because excess detrital matter exported to marine waters sustains food webs, including important fisheries (i.e., Odum?s [1980] ?outwelling hypothesis?). Although physically and biologically similar to saltmarshes elsewhere, Australian coastal saltmarshes have certain unique characteristics (e.g., the tidal zonation of marsh and mangroves and levels of productivity) that natural resource managers need to be aware of. Perhaps more so than elsewhere, the great majority of the Australian population lives along or near the coast. Consequently, Australian saltmarsh environments have been subject to significant human-driven change since European settlement. In spite of these compelling facts, Australian publications remain under-represented relative to the extent of saltmarsh on the continent. Australian Saltmarsh Ecology does much to correct this situation.
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35

Marfai, Muh. „Impact of coastal inundation on ecology and agricultural land use case study in central Java, Indonesia“. Quaestiones Geographicae 30, Nr. 3 (01.09.2011): 19–32. http://dx.doi.org/10.2478/v10117-011-0024-y.

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Impact of coastal inundation on ecology and agricultural land use case study in central Java, Indonesia Focusing on the regional scale, this study provides information concerning the existing ecological problems associated with coastal inundation in the northern part of coastal area in Central Java Province, Indonesia. The objectives of this paper are to map the coastal inundation, to investigate the impact of coastal inundation on coastal environment and ecology, and to assess the impact of inundation on agricultural land use. An integration of techniques, namely neighborhood analysis, iteration operation, and superimposed analysis method has been applied to generate the digital map and to analyze the impact of inundation. Fieldwork measurement has been done using cross-profiling in order to observe the impact of inundation on the coastal ecosystem. Based on the scenario of 100 cm and 150 cm of inundation, the affected area is about 15 207.6 Ha and 16 687.31 Ha, respectively. Fishpond, dry farming and paddy field are the most affected agricultural areas due to coastal inundation.
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36

Lee, Sang Heon, Panthalil S. Bhavya und Bo Kyung Kim. „Marine Nitrogen Fixation and Phytoplankton Ecology“. Water 14, Nr. 10 (20.05.2022): 1638. http://dx.doi.org/10.3390/w14101638.

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37

Barrett-Mold, Claire, und Helene Burningham. „Contrasting ecology of prograding coastal dunes on the northwest coast of Ireland“. Journal of Coastal Conservation 14, Nr. 2 (25.09.2009): 81–90. http://dx.doi.org/10.1007/s11852-009-0069-4.

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38

Schindler, Daniel E., Mark D. Scheuerell, Jonathan W. Moore, Scott M. Gende, Tessa B. Francis und Wendy J. Palen. „Pacific salmon and the ecology of coastal ecosystems“. Frontiers in Ecology and the Environment 1, Nr. 1 (Februar 2003): 31–37. http://dx.doi.org/10.1890/1540-9295(2003)001[0031:psateo]2.0.co;2.

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39

Casey, William H., Albert Guber, Charles Bursey und Curtis R. Olsen. „Chemical controls on ecology in a coastal wetland“. Eos, Transactions American Geophysical Union 67, Nr. 45 (1986): 1305. http://dx.doi.org/10.1029/eo067i045p01305.

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40

King, Stacie M. „Polity and Ecology in Formative Period Coastal Oaxaca“. Journal of Island and Coastal Archaeology 9, Nr. 2 (04.05.2014): 292–94. http://dx.doi.org/10.1080/15564894.2014.921962.

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41

Tett, Paul. „The ecology of plankton in Scottish coastal waters“. Proceedings of the Royal Society of Edinburgh. Section B. Biological Sciences 100 (1992): 27–54. http://dx.doi.org/10.1017/s0269727000011052.

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SynopsisThe lives of the plants, animals and bacteria of the plankton are ruled by the diffusive nature of their fluid medium, in which vertical turbulence is sometimes checked by density gradients caused by surface heating or inflow of freshwater. Seasonal and spatial changes in the production and species composition of phytoplankton and associated microheterotrophs result from interactions amongst light penetration, supply of mineral nutrients, and vertical mixing; many species are capable of rapid increase when multiplication exceeds losses by dispersion and predation. Water depth, currents, dispersion and food supplies control mesozooplankton.Although Scottish coastal waters include a variety of pelagic environments, there is little evidence of site-specific flora or fauna. Planktonic assemblages are, however, locally more diverse than expected. If this excess diversity is a result of ever-changing conditions, the composition of microplanktonic associations may be largely decided by chance. Explanations based on niche theory seem to apply convincingly only to the larger, semi-nektonic, pelagic crustaceans. Thus, consideration of issues relating to conservation raises fundamental and difficult questions about the biology of plankton.Conservation of species is impractical if accident plays a large part in recruitment and replacement. Conversely, the dispersive nature of the pelagic environment and the weakness of interspecific relations may lessen the sensitivity of plankton to anthropogenic perturbations. Nevertheless, eutrophication and climatic change can disturb pelagic communities, especially in enclosed waters.
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42

Yulianda, F., Y. Wardiatno, I. W. Nurjaya und A. Herison. „Coastal Conservation Strategy using Mangrove Ecology System Approach“. Asian Journal of Scientific Research 7, Nr. 4 (15.09.2014): 513–24. http://dx.doi.org/10.3923/ajsr.2014.513.524.

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43

Hinchey, Elizabeth K., Matthew C. Nicholson, Roman N. Zajac und Elizabeth A. Irlandi. „Preface: Marine and coastal applications in landscape ecology“. Landscape Ecology 23, S1 (28.08.2007): 1–5. http://dx.doi.org/10.1007/s10980-007-9141-3.

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44

Ernst, W. H. O. „Some considerations of and perspectives in coastal ecology“. Vegetatio 62, Nr. 1-3 (Juni 1985): 533–45. http://dx.doi.org/10.1007/bf00044779.

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45

Bearzi, Maddalena, Charles A. Saylan und Alice Hwang. „Ecology and comparison of coastal and offshore bottlenose dolphins (Tursiops truncatus) in California“. Marine and Freshwater Research 60, Nr. 6 (2009): 584. http://dx.doi.org/10.1071/mf08279.

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Populations of coastal and offshore bottlenose dolphins (Tursiops truncatus) are considered to differ ecologically, with implications for their protection and management. We assessed occurrence, distribution and behaviour of coastal and offshore populations of dolphins during a photo-identification study in Santa Monica Bay and nearby areas (1997–2007). Bottlenose dolphins occurred year-round and were encountered on 44.2% of all surveys (n = 425). We photo-identified 647 individuals; of these, 375 (58.0%) were coastal (<1 km from shore), 241 (37.2%) offshore (1–65 km from shore) and 31 were both (4.8%). Dolphins mostly travel (69.0%) and travel-dive (61.5%), with offshore dolphins socialising more (22.6%) than coastal. There were low re-sighting rates for both coastal and offshore dolphins. Low re-sighting rates of coastal individuals provide little evidence of year-round site fidelity, suggesting their range is greater than the study area. Several individuals were re-sighted between and over 1-year periods, often foraging. This suggests that coastal dolphins: (1) are highly mobile within inshore waters, but spend time foraging in the study area, and (2) range >1 km from shore, contrary to what has been previously reported.
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46

SEINO, Satoquo. „Coastal environmental conservation-perspectives of ecology and civil engineering at the Japanese coasts“. Ecology and Civil Engineering 3, Nr. 1 (2000): 1–6. http://dx.doi.org/10.3825/ece.3.1.

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47

Marhamah, Ithvi. „Community and City Government Participation in Coastal Coastal Area Conservation: a study in Pariaman City.“ Jurnal Ilmu Sosial Mamangan 9, Nr. 2 (06.05.2021): 90–102. http://dx.doi.org/10.22202/mamangan.v9i2.4444.

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Irregularities in spatial use that are not in accordance with regional planning resulting in reduced protected and buffer zone space in Pariaman City. The research objective was to analyze the causes of the deviation in spatial use from the point of view of the sustainability of the coastal area in Pariaman City. The research method is a combination of qualitative research methods with quantitative research methods using a spatial approach using geographic information systems (GIS). The results show that the harmonization analysis between Law 26 of 2007 article 5 and Law 1 of 2014 article 9 and RTRW are appropriate: Coastal areas are used as protected and buffer areas, but the use of existing land is not in accordance with the harmonization analysis of the two laws and regulations. By the existence of a built-up area in an area that should be a buffer zone. The participation of the community and city government in the management of the coastal area causes this deviation: Lack of knowledge of residents about the zoning of customary rights over are two contributing factors. The city government which prioritizes the economic development of coastal areas with tourism development threatens the ecology and coastal resources Keyword: Environmental Management, Conservation, Coasta areas, Community participation, Zoning
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48

Kshatriya, Gautam Kumar, und Arnab Ghosh. „Undernutrition among the Tribal Children in India: Tribes of Coastal, Himalayan and Desert Ecology“. Anthropologischer Anzeiger 66, Nr. 3 (19.09.2008): 355–63. http://dx.doi.org/10.1127/aa/66/2008/355.

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49

Murray, Shauna, und Iain M. Suthers. „Population ecology of Noctiluca scintillans Macartney, a red-tide-forming dinoflagellate“. Marine and Freshwater Research 50, Nr. 3 (1999): 243. http://dx.doi.org/10.1071/mf98052.

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The population ecology of the large heterotrophic dinoflagellate Noctiluca scintillans Macartney was examined in the coastal ocean and two estuaries in south-eastern Australia from July 1996 to June 1997. High concentrations (>100 cells L–1) occurred in spring and again in late summer, and low concentrations (<5 cells L–1) in mid summer and mid winter. Abundances were greater in coastal waters than in the estuaries during all months in which concentration exceeded 1 cell L–1. During the spring bloom, Noctiluca cells from coastal stations had small diameters (340–450 µm), a high nutritional status and a high proportion of division stages, indicative of good condition. During the late summer blooms, poor-condition cells were found in coastal waters and especially in the near-surface concentrations of red tides (>104 cells L–1), and were characterized by large diameters (400–1200 µm), cell lysis and uniformly low nutritional status; at this time, Noctiluca cells from estuaries were generally fewer, smaller and in better condition. Overall, cell concentrations were higher in coastal waters than in the estuaries, and red tides of Noctiluca probably developed along the local coast (in spring) or were advected into the area from northern regions (in late summer).
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50

Fitriana, Fitriana, Ibrahim Ibrahim und Ranto Ranto. „Ecology-Based Coastal Community Empowerment Innovation in Batu Beriga Village, Central Bangka Regency“. International Journal of Regional Innovation 2, Nr. 3 (01.09.2022): 14–28. http://dx.doi.org/10.52000/ijori.v2i3.54.

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The coastal area is a part that is rich in the potential of marine and coastal resources that can be developed properly. Talking about the coast can not be separated from the existence of people living in coastal areas, since long ago people have also depended on the use of natural resources around the coast and the sea. Over time, the lives of coastal communities have deteriorated and until now coastal communities are identically known as marginalized communities. This condition is accompanied by coastal communities who have not been able to manage marine and coastal resources optimally. This is because the touch of knowledge about the use of resource development in coastal areas is very minimal, As a result, the community does not know how to manage the potential of marine and coastal resources that are more effective and innovative. Therefore, the active role and concern of the government can certainly reduce the powerlessness of coastal communities with the limited capabilities that the community has so far so that coastal communities can get out of the state of powerlessness. which is characterized by the condition of marginalized society. The purpose of this research is to analyze how the form of ecological-based coastal community empowerment is, as well as to find out the implications of ecological-based coastal community empowerment programs, and identify what are the opportunities and challenges in ecological-based coastal community empowerment in Batu Beriga Village, Central Bangka Regency. This study uses the concept of empowerment by Jim Ife as the basic foundation of the research. Regarding the concept of empowerment, according to Jim Ife, with regard to community empowerment, it is providing resources, opportunities, and knowledge to residents to improve their abilities. Empowerment is defined as an effort to provide power (empowerment) and strengthening (strengthening) to the community. This concept has a close relationship with two main concepts, namely (power) which means power and (disadvantaged) which means inequality. The method used in this research is descriptive qualitative with the primary data source coming from unstructured interviews with 15 informants. The informants consisted of 3 village officials, 5 community members, 3 tourism awareness groups in Batu Beriga Village, 2 staff from the Environment and Forestry Service (DLHK) of the Bangka Belitung Islands Province, 2 staff from the Ministry of Environment and Forestry (KLHK) of the Bangka Belitung Islands Province. The results of this study indicate that the empowerment of the Batu Beriga Village community is carried out based on environmental care. The form of community empowerment based on ecology is a manrove planting labor-intensive program. The implication of the program is that it can have a positive impact on social, economic, and environmental aspects, opportunities that occur The results of this study indicate that the empowerment of the Batu Beriga Village community is carried out based on environmental care. The form of community empowerment based on ecology is a manrove planting labor-intensive program. The implication of the program is that it can have a positive impact on social, economic, and environmental aspects, opportunities that occur The results of this study indicate that the empowerment of the Batu Beriga Village community is carried out based on environmental care. The form of community empowerment based on ecology is a manrove planting labor-intensive program. The implication of the program is that it can have a positive impact on social, economic, and environmental aspects, opportunities that occur namely opportunities for mangrove ecosystem rehabilitation and economic recovery opportunities. However, there are challenges such as conflicts of interest, lack of public awareness, and low human resources (HR).
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