Academic literature on the topic 'Seashore ecology'

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Journal articles on the topic "Seashore ecology"

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Symons, N., and M. Jenkins. "Seashore Studies." Journal of Ecology 73, no. 2 (July 1985): 715. http://dx.doi.org/10.2307/2260515.

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Hanley, J. R. "Seashore Ecology by Thomas Carefoot with Rodney D. Simpson [Book Review]." Beagle : Records of the Museums and Art Galleries of the Northern Territory 3, no. 1 (1985): 229–30. http://dx.doi.org/10.5962/p.320157.

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Andersen, Ulla Vogt. "Dispersal strategies of Danish seashore plants." Ecography 16, no. 4 (October 1993): 289–98. http://dx.doi.org/10.1111/j.1600-0587.1993.tb00218.x.

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Schmid, Rudolf, and Donald D. Cox. "A Naturalist's Guide to Seashore Plants: An Ecology for Eastern North America." Taxon 52, no. 2 (May 2003): 395. http://dx.doi.org/10.2307/3647429.

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Wan, Shiuan, and Tsu Chiang Lei. "A Development of a Robust Machine for Removing Irregular Noise with the Intelligent System of Auto-Encoder for Image Classification of Coastal Waste." Environments 9, no. 9 (September 4, 2022): 114. http://dx.doi.org/10.3390/environments9090114.

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Currently, the seashore is threatened by the environment of climate change and increasing coastal waste. The past environmental groups used a large amount of manpower to manage the coast to maintain the seashore environment. The computational time cost and efficiency are not ideal for the vast area of the seashore. With the progress of GIS (Geographic Information System) technology, the ability of remote sensing technology can capture a wide range of data in a short period. This research is based on the application of remote sensing technology combined with machine learning to display the observation of our seashore. However, in the process of image classification, the seashore wastes are small, which required the use of high-resolution image data. Thus, how to remove the noise becomes a crucial issue in developing an image classifier machine. The difficulties include how to adjust the value of parameters for removing/avoiding noises. First, the texture information and vegetation indices were employed as ancillary information in our image classification. On the other hand, auto-encoder is a very good tool to denoise a given image; hence, it is used to transform high-resolution images by considering ancillary information to extract attributes. Multi-layer perceptron (MLP) and support vector machine (SVM) were compared for classifier performance in a parallel study. The overall accuracy is about 85.5% and 83.9% for MLP and SVM, respectively. If the AE is applied for preprocessing, the overall accuracy is increased by about 10–12%.
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Navarro-Rosinés, Pere, and Xavier Llimona. "Belonia Mediterranea, a New Calcicolous Lichen Species From Catalonia (Ne Spain)." Lichenologist 29, no. 1 (January 1997): 15–27. http://dx.doi.org/10.1006/lich.1996.0056.

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AbstractBelonia mediterranea Nav.-Ros. & Llimona sp. nov. is described and compared with other, mainly saxicolous, species of the genus. It is known only from the type locality, Medes Islands (Catalonia, NE Spain), where it occurs on shaded limestone cliffs, near the Mediterranean seashore. It differs from related saxicolous species of Belonia mainly in the appearance of the thallus, ascospore septation and ecology. A key to the European species of Belonia is provided.
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Johnson, Joshua B., and J. Edward Gates. "Bats of Assateague Island National Seashore, Maryland." American Midland Naturalist 160, no. 1 (July 2008): 160–70. http://dx.doi.org/10.1674/0003-0031(2008)160[160:boains]2.0.co;2.

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Harley, Christopher D. G. "Patterns, Pathways, and Processes in Seashore Ecosystems." Ecology 82, no. 12 (December 2001): 3566–67. http://dx.doi.org/10.1890/0012-9658(2001)082[3566:ppapis]2.0.co;2.

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ARUP, Ulf. "Caloplaca sorediella Arup, a new sorediate species from western Britain." Lichenologist 38, no. 6 (October 19, 2006): 499–502. http://dx.doi.org/10.1017/s0024282906006165.

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Wang, Wei, Jie Wang, Francis M. P. Choi, Ping Ding, Xiao‐xu Li, Guo‐dong Han, Meng‐wen Ding, et al. "Global warming and artificial shorelines reshape seashore biogeography." Global Ecology and Biogeography 29, no. 2 (October 16, 2019): 220–31. http://dx.doi.org/10.1111/geb.13019.

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Dissertations / Theses on the topic "Seashore ecology"

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Tai, Koon Keung. "Ecological status and conservation value of soft shore habitats in Hong Kong /." access full-text access abstract and table of contents, 2005. http://libweb.cityu.edu.hk/cgi-bin/ezdb/thesis.pl?mphil-bch-b19885970a.pdf.

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Thesis (M.Phil.)--City University of Hong Kong, 2005.
"Submitted to Department of Biology and Chemistry in partial fulfillment of the requirements for the degree of Master of Philosophy" Includes bibliographical references (leaves 143-161)
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Soares, Alexandre Goulart. "Sandy beach morphodynamics and macrobenthic communities in temperate, subtropical and tropical regions : a macroecological approach." Thesis, University of Port Elizabeth, 2003. http://hdl.handle.net/10948/293.

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A comprehensive study involving 52 microtidal beaches spanning from reflective to dissipative states and located in tropical, subtropical and temperate regions in the Atlantic, Pacific and Indian oceans was carried out to unravel the relative roles of latitude and beach morphodynamics in determining beach macrobenthic species richness, abundance, biomass and mean individual body sizes. Since beach slope is one of the most important factors controlling beach fauna, a model based on beach geometry was applied to the sub-aerial beach deposit to understand the role of physical factors in predicting equilibrium beach slopes. Additionally, it was tested if the occurrence of beach types is related to latitude, and how physical factors change with morphodynamics and latitude. The beach morphometric model makes three assumptions: 1) that the cross-section of a beach deposit is equivalent to a right-angled triangle, 2) that the physical hydrodynamic factors (wave height and spring tide amplitude) and the beach deposit characteristics (sand grain size, beach slope and width) are interchangeable with their geometric counterparts producing an equation to explain beach geometry, and 3) that the predicted beach slope is in equilibrium with the hydrodynamic and sedimentological forces. The equation for predicting beach slope was derived and then tested against field data collected over 52 beaches. The predicted slopes were not significantly different from the observed slopes of the studied natural beaches. However some estimated slopes were different than observed ones. Possible sources of deviation between calculated and observed slopes may be the systematic sampling errors associated with field data. Alternatively, observed slopes could be the result of past hydrodynamic conditions, explaining the differences with the slopes calculated by the beach morphometric model, which assumes a state of equilibrium between beach slope and hydrodynamic conditions. A higher correlation of beach faunal structure with observed slopes rather than with present hydrodynamic conditions could then be indicative of faunal responses to previous hydrodynamic conditions in the same way was the observed slopes. The beach morphometric model could therefore be also useful in predicting faunal responses to changing hydrodynamic conditions. Since the model does not consider wave period, it is concluded that further tests should be done using laboratory and time-series field data and incorporating the role of wave period and beach permeability to ascertain its predictive value. Tropical regions had significantly more beaches in a reflective state than temperate and subtropical regions. Some tropical beaches were fronted by coral reefs, which not only provided coarse carbonate particles, but also additionally dissipated the low wave energy present in these climatic areas. Only one dissipative beach with high energy was found in the tropics, in southeast Madagascar. Temperate and subtropical regions, on the other hand, were dominated by dissipative beaches with medium to fine sands. Open oceanic reflective beaches were non-existent in the subtropics and rare in temperate regions, only occurring in estuaries, enclosed bays or on islands facing the continent. Intermediate beaches were more common in the subtropics but also occurred frequently in the other two regions, having higher energy in temperate regions. Reflective beaches had significantly steeper slopes, coarser sands, smaller waves and shorter swash lengths when compared to dissipative beaches. Additionally, reflective beaches were narrower, had deeper water tables and in consequence shorter saturation zones. Wave periods and surfzone widths were on average larger on dissipative than on reflective beaches. The frequency of occurrence of beach types is therefore related to the climatic signature of each latitude. Mid latitudes would be predicted to have more dissipative beaches with large and long waves because of their proximity to the storm generating belt around 50-60° S - these beaches will have a predominantly finer sands because of the input by rivers in rainy areas. Lower latitudes will have more reflective beaches due to a modal low energy wave climate and also because of the presence of inshore and offshore biotic structures such as coral reefs that dissipate even more the energy from the waves. Tropical and subtropical regions had larger marine species pools than temperate regions. After controlling for biogeographical differences in total species pool, dissipative beaches were on average significantly richer than intermediate and reflective beaches. Crustaceans were also more diverse on dissipative beaches, this difference being not significant for either molluscs or polychaetes. Significant relationships were found between total beach species richness (with or without terrestrial species), crustacean and mollusc species richness with beach morphodynamics as represented by the Dean’s index. Indices incorporating the role of tide, such as BSI, were less important in predicting species richness on the microtidal beaches studied here. Several other physical factors were also significantly correlated with species richness, the most important being the Beach Deposit Index, i.e. BDI, a composite index of beach slope and grain size. The highest correlation was between BDI and relative species richness, i.e. local beach species richness / regional species richness. Total regional marine species richness was higher in Madagascar and North Brazil (tropical beaches) than in Southeast Brazil (subtropical), or the West Coast of South Africa and South-Central Chile (temperate beaches). Not only was the pool of species capable of colonizing beaches richer in tropical and subtropical regions, but also local diversity of each morphodynamic beach type was higher among tropical beaches than their temperate counterparts. Although the results of this study agree with the predictions of the swash exclusion hypotheses, several reflective and intermediate beaches had higher species richness than predicted before and this seems to be linked to the presence of finer sediments and a less turbulent flow for larvae to settle. It is concluded that beach species richness is not necessarily controlled by one major morphodynamic parameter; this control is complex and probably involves multiple interacting biotic (biological interactions) and abiotic (e.g. grain size, wave height, beach slope and width, water table) factors. Species richness seems to be controlled on two different scales: on an evolutionary one where tropical and subtropical regions have higher regional and local diversity due to higher speciation rates; and on an ecological scale, where fine grained sand beaches have their carrying capacity enhanced by higher larval settlement rates and survival of recruits towards adulthood. On average dissipative beaches had higher total densities and macrofaunal abundances than reflective ones. Crustaceans, terrestrial species and cirolanid isopods such as Excirolana spp. were also more abundant on dissipative beaches. The difference was not significant for molluscs and polychaetes. Significant relationships were found between total abundance, crustacean species richness and beach morphodynamics as represented by the Dean’s index. Again, BSI was less important than individual physical factors in determining faunal abundance on the studied microtidal beaches. Several other physical factors were also significantly correlated with abundance, the most important being the Beach Deposit Index (BDI). The highest correlation was between BDI and total macrofaunal abundance. Factors related to surf zone processes, and possibly productivity, were highly correlated with total community, crustaceans, Excirolana spp. and terrestrial species abundances. The abundances of polychaetes and molluscs were better correlated with factors related to the beach deposit (BDI, slope, grain size and water table depth). Significant differences were observed between latitudinal regions for the average beach and also for each beach type. In general temperate beaches harboured larger community densities and abundances, and also crustacean, Excirolana spp. and terrestrial abundances. Mollusc and polychaete abundances were larger on subtropical and tropical beaches. The control of abundance on a sandy beach is complex and involves multifactorial processes at evolutionary and ecological scales. At evolutionary scales animals seem to attain higher abundances in the region where they first evolved, e.g. amphipods and isopods in temperate regions. At ecological scales they attain higher abundances where productivity is higher (total macrofaunal, crustaceans, Excirolana spp., terrestrial spp.) or where the settlement environment is more benign (molluscs and polychaetes). Dissipative beaches supported larger average and total community biomass than reflective beaches. Crustaceans, terrestrial species and cirolanid isopods such as Excirolana spp. also had larger biomass on dissipative beaches. The difference was not significant for molluscs and polychaetes. Significant relationships were found between the biomass of community and taxonomic groups with beach morphodynamics as represented by the Dean’s morphodynamic index. On the microtidal beaches studied here, BSI was less important than other morphodynamic indices and single physical factors in determining faunal biomass and mean individual body size. Surf zone characteristics such as wave height, period and surf zone width had the highest correlations with community, crustacean.
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Cheung, Ka Chung. "Effects of eutrophication on soft shore benthic community /." access full-text access abstract and table of contents, 2005. http://libweb.cityu.edu.hk/cgi-bin/ezdb/thesis.pl?mphil-bch-b1988770xa.pdf.

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Thesis (M.Phil.)--City University of Hong Kong, 2005.
"Submitted to Department of Biology and Chemistry in partial fulfillment of the requirements for the degree of Master of Philosophy" Includes bibliographical references (leaves 153-181)
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Cheung, Pui-shan Catherine. "An intertidal survey of Cape d'Aguilar, Hong Kong with special reference to the ecology of high-zoned rock pools /." [Hong Kong] : University of Hong Kong, 1991. http://sunzi.lib.hku.hk/hkuto/record.jsp?B13028352.

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Kaminsky, George M. "Shoreface behaviour and equilibrium." Phd thesis, School of Geosciences, 2006. http://hdl.handle.net/2123/10309.

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Marin, Jarrin Jose R. 1980. "The Ecology of Surf Zone Fauna of Dissipative Sandy Beaches in Southern Oregon U.S.A." Thesis, University of Oregon MS Thesis, 2007. http://hdl.handle.net/1794/5232.

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Loegering, John P. "Piping plover breeding biology, foraging ecology and behavior on Assateague Island National Seashore, Maryland." Thesis, This resource online, 1992. http://scholar.lib.vt.edu/theses/available/etd-09052009-040402/.

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Cheung, Ma Shan. "Trophic transfer of metals along marine rocky shore food chains /." View abstract or full-text, 2007. http://library.ust.hk/cgi/db/thesis.pl?AMCE%202007%20CHEUNG.

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Van, Herwerden L. "Human recreational activity and its impact on a metropolitan coastline." Master's thesis, University of Cape Town, 1989. http://hdl.handle.net/11427/14356.

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Recreation has an important social function in modern societies, with ever-increasing pressures in the day-to-day life being felt by most people. This study addresses the impact of recreational activity on metropolitan shorelines, with particular reference to the False Bay shoreline. During summer holiday periods shoreline utilization in the Western Cape peaks on the public holidays of 26 December, 1 and 2 January, beach attendances reaching levels of 2 to 10 times higher than attendances on other days during the summer holidays. The greatest proportion of visitors to the beach (94%) engage in non-exploitative activities, such as sunbathing and swimming. Most visitors occur on the beaches between 12h00 and 16h00, week-ends being most popular during out-of-season periods, but in-season week day attendances exceed those of weekends. Only 6% of visitors surveyed were engaged in exploitative activities such as angling and bait- or food-gathering. Conservation awareness of visitors to the shore is related to the place of residence of the person, as well as activity engaged in by the person. Fish numbers and their size frequency distributions in protected areas differs to those of unprotected areas. If boulders on a sheltered shore are over-turned during bait gathering it has an adverse effect on the boulder communities, whether the boulders are replaced or left over-turned. When bait gatherers target on mussel-worms as bait, they may cause inadvertent damage to the primary matrix of mussel bed or tube-worm reef in the process, thereby affecting ecological succession processes in the intertidal environment. Management of metropolitan shorelines must therefore provide for quality recreational experiences, while applying conservation measures to selected areas that are susceptible to over-exploitation under the onslaught of ever-increasing numbers of recreationists. For such measures to be of any benefit to the marine environment, it is essential that people are not only informed, but that the regulations are also properly enforced.
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Bliesner, Kasey Lauren. "Trophic ecology and bioenergetics modeling of Sacramento perch (Archoplites interruptus) in Abbotts Lagoon, Point Reyes National Seashore /." Online Access, 2005. http://www.humboldt.edu/~cuca/documents/theses/bliesnerthesis.pdf.

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Books on the topic "Seashore ecology"

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1944-, Simpson Rodney D., and Carefoot Thomas 1938-, eds. Seashore ecology. St. Lucia: University of Queensland Press, 1985.

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Sayre, April Pulley. Seashore. New York: Twenty-First Century Books, 1996.

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Bowman, Lucy. Seashore. New York: Scholastic, 2009.

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Morris, Neil. Seashore explorer. Oxford: Raintree, 2004.

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National Geographic Society (U.S.). Special Publications Division., ed. America's seashore wonderlands. Washington, D.C: The Society, 1985.

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National Geographic Society. Special Publications Division., ed. America's seashore wonderlands. Washington, D.C: The Society, 1985.

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Raffaelli, D. G. Intertidal ecology. 2nd ed. Dordrecht: Kluwer Academic Publishers, 1999.

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Swallow, Su. The seashore. London: Usborne, 2006.

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Cooper, Ann. Along the seashore. Denver: Denver Museum of Natural History Press, 1997.

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Steve, Parker. Seashore. Parkwest, N.Y: BBC, 1992.

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Book chapters on the topic "Seashore ecology"

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Slingsby, David, and Ceridwen Cook. "Seashore Habitats." In Practical Ecology, 171–90. London: Macmillan Education UK, 1986. http://dx.doi.org/10.1007/978-1-349-08226-1_10.

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Jerling, Lenn. "Population dynamics of Plantago maritima along a distributional gradient on a Baltic seashore meadow." In Ecology of coastal vegetation, 155–61. Dordrecht: Springer Netherlands, 1985. http://dx.doi.org/10.1007/978-94-009-5524-0_16.

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Panisi, Martina, Ricardo F. de Lima, Jezreel do C. Lima, Yodiney dos Santos, Frazer Sinclair, Leonor Tavares, and David T. Holyoak. "Terrestrial Mollusca of the Gulf of Guinea Oceanic Islands." In Biodiversity of the Gulf of Guinea Oceanic Islands, 407–29. Cham: Springer International Publishing, 2022. http://dx.doi.org/10.1007/978-3-031-06153-0_16.

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AbstractThe oceanic islands of the Gulf of Guinea are known for their remarkable endemic species richness, and the terrestrial Mollusca group is particularly distinctive. This chapter summarizes the exploration and diversity of this group, discussing biogeography, evolution, ecology, and conservation to identify persisting knowledge gaps. Terrestrial malacological studies in the Gulf of Guinea islands started at the end of the eighteenth century but have been intermittent. Recent systematic surveys have continued to find novelties, and the most recent revision lists 96 species, of which 62 are endemic: Príncipe has 40 terrestrial (60% single-island endemic) and five seashore species, São Tomé has 52 terrestrial (50% single-island endemic) and seven seashore species, Annobón has 14 terrestrial species (50% single-island endemic), 3 species are endemic to Príncipe and São Tomé, and 2 are endemic to the three islands. The islands were colonized by diverse “clades” arriving from continental Africa, which is consistent with biogeographical patterns from other taxonomic groups. However, in line with Mollusca dispersal limitations, inter-island colonization seems to be less frequent, while there are multiple cases of speciation within the same island. The land snail assemblage on São Tomé seems to be strongly structured by land-use type: endemics being associated mostly with forest and non-endemics to anthropogenically modified environments. Only 13 species have been recorded across the altitudinal range of São Tomé, suggesting altitude is also essential to determining species distribution. Habitat loss and introduced species are important threats, but so far, only the endemic Archachatina bicarinata has been listed as threatened. Despite recent progress, further studies are still needed to better understand this unique fauna and inform conservation strategies.
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Tait, R. V., and F. A. Dipper. "The seashore." In Elements of Marine Ecology, 256–312. Elsevier, 1998. http://dx.doi.org/10.1016/b978-075062088-8/50008-1.

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Dipper, Frances. "Benthic living: the seashore." In Elements of Marine Ecology, 257–318. Elsevier, 2022. http://dx.doi.org/10.1016/b978-0-08-102826-1.00001-6.

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"Seashores and Woodlands: Looking for Patterns." In Shaping Ecology, 60–79. Oxford, UK: Wiley-Blackwell, 2012. http://dx.doi.org/10.1002/9781118290927.ch6.

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"Energy Flow, Food Webs, and Material Cycling." In The Ecology of Seashores, 367–436. CRC Press, 2000. http://dx.doi.org/10.1201/9781420042634-9.

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"The Environment." In The Ecology of Seashores, 13–30. CRC Press, 2000. http://dx.doi.org/10.1201/9781420042634-4.

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"Control of Community Structure." In The Ecology of Seashores, 287–366. CRC Press, 2000. http://dx.doi.org/10.1201/9781420042634-8.

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"Soft Shores." In The Ecology of Seashores, 97–248. CRC Press, 2000. http://dx.doi.org/10.1201/9781420042634-6.

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