Academic literature on the topic 'Intertidal ecology'

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Journal articles on the topic "Intertidal ecology"

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Schlacher, Thomas, David Raffaelli, and Stephen Hawkins. "Intertidal Ecology." Estuaries 21, no. 2 (June 1998): 365. http://dx.doi.org/10.2307/1352485.

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Moore, P. G. "Intertidal ecology." Journal of Experimental Marine Biology and Ecology 217, no. 1 (September 1997): 137–38. http://dx.doi.org/10.1016/s0022-0981(96)02765-7.

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Berlow, Eric L. "Intertidal ecology." Trends in Ecology & Evolution 12, no. 8 (August 1997): 329–30. http://dx.doi.org/10.1016/s0169-5347(97)89926-0.

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Barnes, R. S. K., and L. Claassens. "Do beds of subtidal estuarine seagrass constitute a refuge for macrobenthic biodiversity threatened intertidally?" Biodiversity and Conservation 29, no. 11-12 (July 22, 2020): 3227–44. http://dx.doi.org/10.1007/s10531-020-02019-0.

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Abstract Biodiversity differentials between macrobenthic assemblages associated with adjacent intertidal and subtidal areas of a single seagrass system were investigated for the first time. Assemblage metrics of conservation relevance—faunal abundance and its patchiness, faunal richness, and beta diversity—were examined at four contrasting dwarf-eelgrass localities in the Knysna estuarine bay, part of South Africa's Garden Route National Park but a system whose intertidal areas are heavily impacted anthropogenically. Faunal assemblages were significantly different across all localities and between subtidal and intertidal levels at each locality although their taxonomic distinctness was effectively constant. Although, as would be expected, there were clear trends for increases in overall numbers of species towards the mouth at all levels, few generalities relating to the relative importance of the subtidal seagrass habitat were evident across the whole system—magnitude and direction of differentials were contingent on locality. Shore-height related differences in assemblage metrics were minor in the estuarine and lagoonal zones but major in the marine compartment, although the much greater subtidal faunal abundance there was largely consequent on the superabundance of a single species (the microgastropod Alaba pinnae), intertidal zones then displaying the greater species diversity due to greater equitability of species densities. Along its axial channel, the Knysna subtidal seagrass does not support richer versions of the intertidal polychaete-dominated assemblages fringing it; instead, it supports different and more patchily dispersed gastropod-dominated ones. At Knysna at least, the subtidal hardly constitutes a reservoir of the seagrass biodiversity present intertidally.
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Denny, M. W., and R. T. Paine. "Celestial Mechanics, Sea-Level Changes, and Intertidal Ecology." Biological Bulletin 194, no. 2 (April 1998): 108–15. http://dx.doi.org/10.2307/1543040.

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Garza, Corey. "Landscape Ecology in the Rocky Intertidal: Opportunities for Advancing Discovery and Innovation in Intertidal Research." Current Landscape Ecology Reports 4, no. 3 (June 25, 2019): 83–90. http://dx.doi.org/10.1007/s40823-019-00042-8.

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Manzur, Tatiana, Mario Barahona, and Sergio A. Navarrete. "Ontogenetic changes in habitat use and diet of the sea-star Heliaster helianthus on the coast of central Chile." Journal of the Marine Biological Association of the United Kingdom 90, no. 3 (October 19, 2009): 537–46. http://dx.doi.org/10.1017/s0025315409990786.

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Ontogenetic shifts in habitat use and diet are ubiquitous in nature and usually have profound consequences for the ecology and evolution of the species. In the case of species with strong interactions within their communities, such as keystone predators, understanding this kind of size-related change is critical to understand variation and connectivity among spatially distinct habitats of coastal communities. Yet the ecology of early life stages of marine benthic invertebrates, particularly asteroids, is poorly understood. Here we describe the results of surveys to characterize the habitat and quantify the abundance and diet of recruits of the sun star Heliaster helianthus, a keystone predator at rocky intertidal sites in central Chile. Our results support the existence of size-related, ontogenetic changes in habitat use and diet of this species. Recruits occupy boulders and crevices in the high or mid-high intertidal zones of wave-protected habitats and as they grow they move down towards lower tidal levels. Adults are characteristically found in the low intertidal zone of wave exposed and semi-exposed habitats. These changes in habitat use are accompanied by changes in diet composition and particularly by a broadening of the prey species incorporated in the diet. Since early stages of Heliaster appear to be most sensitive to predation and abiotic stress and since adults are such important predators in wave exposed rocky shores, knowledge of the basic ecology of early stages of this species is critical to fully understand the dynamics of intertidal communities.
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Wares, John P., and Clifford W. Cunningham. "PHYLOGEOGRAPHY AND HISTORICAL ECOLOGY OF THE NORTH ATLANTIC INTERTIDAL." Evolution 55, no. 12 (2001): 2455. http://dx.doi.org/10.1554/0014-3820(2001)055[2455:paheot]2.0.co;2.

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Reddin, Carl J., Felipe Docmac, Nessa E. O’Connor, John H. Bothwell, and Chris Harrod. "Coastal Upwelling Drives Intertidal Assemblage Structure and Trophic Ecology." PLOS ONE 10, no. 7 (July 27, 2015): e0130789. http://dx.doi.org/10.1371/journal.pone.0130789.

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Wares, John P., and Clifford W. Cunningham. "PHYLOGEOGRAPHY AND HISTORICAL ECOLOGY OF THE NORTH ATLANTIC INTERTIDAL." Evolution 55, no. 12 (December 2001): 2455–69. http://dx.doi.org/10.1111/j.0014-3820.2001.tb00760.x.

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Dissertations / Theses on the topic "Intertidal ecology"

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Chavanich, Suchana. "Rocky intertidal zonation and habitat ecology of gammaridean Amphipods in Long Island Sound /." Click for abstract, 1997. http://library.ctstateu.edu/ccsu%5Ftheses/1484.html.

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Thesis (M.A.)--Central Connecticut State University, 1997.
Thesis advisor: Dr. Kim A. Wilson. " ... in partial fulfillment of the requirements for the degree of Master of Arts in Biology." Includes bibliographical references (leaves 47-56).
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Ramon, Marina L. "Molecular ecology and evolution of intertidal sculpins /." Diss., Digital Dissertations Database. Restricted to UC campuses, 2007. http://uclibs.org/PID/11984.

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Murias, dos Santos Antonio E. Ferrand de Almeida. "Intertidal ecology of northern Portuguese rocky shores." Thesis, University of Southampton, 2000. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.326590.

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McGary, Cara L. "A long term comparison of rocky intertidal communities in Redwood National and State Parks /." California : Humboldt State University, 2005. http://hdl.handle.net/2148/22.

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Tong, Lily K. Y. (Lily Kit Ying). "The population ecology of the intertidal bivalve Lasaea australis." Phd thesis, Faculty of Arts, 1990. http://hdl.handle.net/2123/9035.

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Dunmore, Robyn Ann. "Demography of early life stages of habitat-forming intertidal fucoid algae." Thesis, University of Canterbury. Biological Sciences, 2006. http://hdl.handle.net/10092/1364.

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The intertidal zone is finely partitioned in species distributions and abundances. The demographies of key species over varying spatial and temporal scales are fundamental to understanding the population structure and overall dynamics of habitats and assemblages. In this thesis, settlement, dispersal and early life stage survival and growth were examined in several habitat-forming intertidal fucoid algae in New Zealand and Oregon, U.S.A. Natural settlement patterns of Hormosira banksii, Cystophora torulosa and Cystophora scalaris were quantified for over three years at a semi-protected shore in southern New Zealand. Settlement was monitored in four tidal zones, within bare rock and algal habitats. Settlement was synchronous between tidal zones but the density of settlement varied spatially and temporally. There were significant differences between tidal zones, habitats and times of the year. For H. banksii, small pulses of settlement occurred year-round with greatest densities during spring and early summer. Greatest settlement occurred at low tidal zones and under adult canopies. Both Cystophora species also reproduced year-round, but had much lower settlement densities than H. banksii. Most settlement occurred during spring and summer, while only small pulses occurred in autumn and winter months. Most settlement was in the lowest tidal zone (0.4 m above chart datum), with only a few zygotes settling at higher shore zones. Canopy cover had no significant effect on settlement densities. Dispersal was examined in Durvillaea spp., H. banksii, C. torulosa and Fucus gardneri. For all species, settlement densities declined with distance from the source populations, but densities were variable between species. Durvillaea spp. dispersal was more extensive than expected, with significant settlement occurring 32 m from the source population, the maximum sample range of the study. However, settlement densities were much higher within 8 m from the source. The extensive dispersal of Durvillaea spp. is a result of the combination of small, slowly sinking eggs and the presence of buoyant mucilage. The other species studied showed far more restrictive dispersal, and much lower settlement densities. Settlement occurred 2 m from the source, but most settlement occurred under or near the canopy. The eggs of these species are much larger and sink faster than the eggs of Durvillaea spp. The consequences of settling at different shore heights and seasons were examined in H. banksii and D. antarctica in New Zealand, and F. gardneri and Pelvetiopsis limitata in Oregon. Transplant experiments tested the effects of grazing and heat/desiccation stress on survival and growth of germlings at different shore heights, during different seasons. High germling mortality was a feature of all species, but rate of mortality depended on conditions and species. There is a trade-off for settling at different times of the year; overall, growth was faster in warmer seasons, but survival was better in cooler seasons. During cooler seasons, germlings are exposed to less heat/desiccation stress, but their slow growth exposes them to grazing and competitive interactions for longer periods. For New Zealand species, shore height had large effects, with better survival and growth in the low shore. Grazers were very effective in the low shore, and heat/desiccation stress had strong effects in the mid and high shores. For Oregon species, effects of grazing and heat/desiccation stress were generally weaker than for New Zealand species. Shore height had weak effects, but ultimately low shore germlings had poor survival, primarily because of overgrowth by ephemeral algae. This is in contrast to the generalisation that survival and growth in the low shore should be better due to a more benign environment. In this study, species had specific demographies that related to their life history characteristics and responses to the local environment. Differences in settlement, dispersal abilities, survival and growth over small spatial and temporal scales clearly underpinned large scale differences in recruitment and adult distribution and abundances.
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Ragnarsson, Stefan Aki. "Successional patterns and biotic interactions in intertidal sediments." Thesis, University of Aberdeen, 1996. http://digitool.abdn.ac.uk/R?func=search-advanced-go&find_code1=WSN&request1=AAIU078135.

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The main objective of this thesis was to investigate the role of biotic interactions, biogenic structures and successional patterns in several invertebrate soft bottom assemblages in the Ythan estuary, Aberdeenshire, Scotland. The seasonal dynamics of the fauna found within a dense tube-field of Lanice conchilega were investigated. The abundance and composition of this fauna differed from that in the adjacent sediments and from that in the nearby sandflat at Red Inches. No consistent differences in abundance could be detected for any species throughout the tube-field, and the mussel (Mytilus edulis) was the only species significantly positively correlated with Lanice tube density. Pygospio elegans was found in significantly reduced numbers in tube-field areas affected by weed. Accumulation of weed and subsequent settlement of mussels in summer and periodical intense sediment movement during winter may have partly accounted for the large seasonal fluctuations seen in the abundance and composition of the tube-field fauna. The size of distributed patches is thought to influence the rate of colonization, but there have been few experimental tests of this proposition. The hypothesis was therefore tested by a field experiment where the rates and modes of colonization of azoic patches of different size (1600cm2 vs. 55cm2) were compared. The results of this experiment were also considered when designing subsequent experiments (see below). None of the invertebrates recorded differed significantly in abundance between patch size on any sampling occasion. The total number of species and individuals rapidly attained control (natural sediment) values. However, the patterns of colonization of individual species could be categorised into three types. The abundances of Type I species mirrored closely those in control sediments. Type II species were opportunists, such as the polychaete Capitella spp., which exceeded the control density rapidly but then showed a decline. Type III species, such as the polychaete Pygospio elegans, showed a very slow increase in azoic areas and never attained control densities, although size distributions were markedly different between the two patch sizes. This experiment showed that over the range studied, size of patch was not important in determining overall colonization patterns on sandflats.
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Hurd, Catriona L. "The physiological ecology of nutrient uptake by intertidal fucoid algae." Thesis, Queen's University Belfast, 1990. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.332658.

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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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Dower, Katherine Mary. "Sand inundation on rocky shores : its effects on species richness and the structure of species assemblages." Thesis, Rhodes University, 1990. http://hdl.handle.net/10962/d1007183.

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Although sand deposits are present on many intertidal rocky shores, their effects on species richness, zonation and trophic structure have often been overlooked. This study is the first to recognise sand as an important abiotic factor on South African rocky shores. Rocky shores in the eastern Cape Province of South Africa are subject to extensive sand inundation and are composed of two hard substrata of differing topographies. Four sites on one substratum and six on the other were sampled quantitatively using quadrats. The biota were identified, counted and/ or weighed to provide a matrix of species biomass and numbers in separate zones. This matrix was then analysed using ordination and classification. A total of 321 species were identified which is more than local rocky or sandy shores. While the intermediate disturbance hypothesis would predict high species richness on these shores, it does not fully explain this richness nor the distribution of species assemblages. Habitat heterogeneity, including the dynamics of sand deposits, is strongly influenced by substratum topography and is the most important factor generating species richness. Abrasion by sand (sand scour) causes local reductions in richness but the presence of semi-permanent sand deposits allows habitation by psammophilic and sand-dependent species. As a result the biota of a sand inundated rocky shore includes both a full rocky shore and a large sandy beach component. Substratum topography controls patterns of sand deposition and retention and community analysis showed that samples were clustered primarily according to species richness and secondarily according to substratum type. Ordination of species identified an arc of species assemblages of decreasing levels of sand tolerance. These corresponded to sample groupings so that th assemblages found in various habitats were characterised by particular levels of sand tolerance. The presence of sand has a negative effect on the biomass of primary producers and filter feeders but a positive effect on the biomass of deposit feeders. Because sand is retained to different degrees in different zones, trophic structure varies between zones and to a lesser extent, between rock types. In general, however, the trophic structure of sand inundated rocky shores is similar to that of non-inundated shores.
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Books on the topic "Intertidal ecology"

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

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Raffaelli, David, and Stephen Hawkins. Intertidal Ecology. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1489-6.

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J, Hawkins S., ed. Intertidal ecology. London: Chapman & Hall, 1996.

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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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McCrae, Jean. Plants and animals of Oregon's rocky intertidal habitat. Newport, OR: Oregon Dept. of Fish and Wildlife, 1989.

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1951-, Rosenfeld Anne Wertheim, ed. Wave-swept shore: The rigors of life on a rocky coast. Berkeley: University of California Press, 2006.

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Hayward, P. J. Animals on seaweed. Richmond, Surrey, England: Richmond Pub. Co., 1988.

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Mohler, June E. Guide to Oregon's rocky intertidal habitats. Newport, OR: Oregon Dept. of Fish and Wildlife. Marine Resources Program, 1997.

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author, Komemoto Ken-ichi joint, Funayama Nobutaka joint author, and Kyōto Daigaku. Seto Rinkai Jikkenjo, eds. A record of the intertidal malacofauna of Cape Bansho, Wakayama, Japan, from 1985 to 2010. [Shirahama-chō, Wakayama-ken, Japan]: Seto Marine Biological Laboratory, Field Science Education and Research Center, Kyoto University, 2011.

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Gardiner, William Wood. Sea surface films: Deposition and toxicity in intertidal habitats. Mount Vernon, Wash: Padilla Bay National Estuarine Research Reserve, 1992.

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Book chapters on the topic "Intertidal ecology"

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Raffaelli, David, and Stephen Hawkins. "The shore environment: major gradients." In Intertidal Ecology, 1–35. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-009-1489-6_1.

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Raffaelli, David, and Stephen Hawkins. "Patterns of distribution." In Intertidal Ecology, 36–70. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-009-1489-6_2.

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Raffaelli, David, and Stephen Hawkins. "Causes of zonation." In Intertidal Ecology, 71–97. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-009-1489-6_3.

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Raffaelli, David, and Stephen Hawkins. "Community dynamics." In Intertidal Ecology, 98–146. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-009-1489-6_4.

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Raffaelli, David, and Stephen Hawkins. "Coping with the physical and biological environment." In Intertidal Ecology, 147–84. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-009-1489-6_5.

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Raffaelli, David, and Stephen Hawkins. "The shore as a system." In Intertidal Ecology, 185–213. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-009-1489-6_6.

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Raffaelli, David, and Stephen Hawkins. "Human impact on the shore." In Intertidal Ecology, 214–54. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-009-1489-6_7.

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Raffaelli, David, and Stephen Hawkins. "Studying shores." In Intertidal Ecology, 255–83. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-009-1489-6_8.

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Kon, Koetsu, Motohiro Shimanaga, and Masahiro Horinouchi. "Marine Ecology: Intertidal/Littoral Zone." In Japanese Marine Life, 241–54. Singapore: Springer Singapore, 2020. http://dx.doi.org/10.1007/978-981-15-1326-8_20.

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Schizas, Nikolaos V., and Thomas C. Shirley. "Autecology of an intertidal Alaskan harpacticoid copepod Apolethon sp." In Ecology and Morphology of Copepods, 361–67. Dordrecht: Springer Netherlands, 1994. http://dx.doi.org/10.1007/978-94-017-1347-4_46.

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Conference papers on the topic "Intertidal ecology"

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Gordon, D. "Intertidal Ecology and Tidal Power Impacts." In OCEANS '87. IEEE, 1987. http://dx.doi.org/10.1109/oceans.1987.1160705.

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Weinmann, Anna E., Susan T. Goldstein, Maria V. Triantaphyllou, and Martin R. Langer. "ECOLOGY AND COMMUNITY STRUCTURE OF MODERN INTERTIDAL FORAMINIFERA FROM CORFU ISLAND (GREECE): INSIGHTS FROM PROPAGULE EXPERIMENTS." In GSA Annual Meeting in Phoenix, Arizona, USA - 2019. Geological Society of America, 2019. http://dx.doi.org/10.1130/abs/2019am-334247.

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Dick, Kaitlin Louise, and Angelos K. Hannides. "THE IMPACT OF PHYSICAL AND MINERALOGICAL PROPERTIES OF INTERTIDAL SANDS AND RESULTANT MICROBIAL ECOLOGY ON THE USE AND MODIFICATION OF LAND DERIVED SUBSTANCES." In 68th Annual GSA Southeastern Section Meeting - 2019. Geological Society of America, 2019. http://dx.doi.org/10.1130/abs/2019se-327599.

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