Article

The Ecology of a New England Salt Marsh

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Abstract

The saltmarsh at Rumstick Cove, Rhode Island, is characterized by a description of the vegetation zones as well as distinct vegetation patches, which it is suggested may arise from a combination of environmental variation and competitive interactions. Competitive relationships are determined chiefly by morphology and the timing of spring emergence of different species. Examples are given of this and of the non-tolerance of some saltmarsh grasses and mussels to the high salt and low oxygen concentration conditions found in the "low marsh' environment. The stages in colonization of bare patches by saltmarsh grasses are discussed, emphasizing competitive, but also cooperative, processes. -J.W.Cooper

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... Salt marshes have been found to produce larger and more variable CH 4 and CO 2 fluxes than adjacent sandy intertidal zones (Hirota et al. 2007). They are defined by strong physical gradients in tidal flushing, salinity, and elevation along which major shifts in plant community composition occur (Nixon 1982, Bertness 1992). Therefore, rates of carbon exchange between the ecosystem and atmosphere may be highly variable across a marsh landscape. ...
... The aerenchyma facilitates bidirectional gas exchange and therefore may increase fluxes of GHGs between anoxic marsh soils where microbes are active and the atmosphere. Historically, at the higher elevations, denser, more shallowly rooted species (Distichlis spicata, Spartina patens, Juncus gerardii) better competed for the least stressful habitats (Bertness 1992, Bertness andLeonard 1997). Their smaller stature and less extensive ventilation of marsh soils may translate into lower GHG fluxes. ...
... Our findings illustrate the potential for CO 2 fluxes to mirror visible differences in plant communities across a coastal marsh landscape. Although multiple edaphic properties often vary across marsh zones (Nixon 1982, Bertness 1992, our zonation gradient in Sage Lot Pond was mainly characterized by relatively subtle differences in surface soil moisture and sulfide and no significant differences in other key variables (salinity, pH; Tables 5 and 6). In contrast, plant community composition and aboveground structural properties (Tables 3 and 4) and belowground biomass (Fig. 5) were markedly different. ...
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Coastal wetlands are major global carbon sinks; however, they are heterogeneous and dynamic ecosystems. To characterize spatial and temporal variability in a New England salt marsh, greenhouse gas (GHG) fluxes were compared among major plant-defined zones during growing seasons. Carbon dioxide (CO2) and methane (CH4) fluxes were compared in two mensurative experiments during summer months (2012-2014) that included low marsh (Spartina alterniflora), high marsh (Distichlis spicata and Juncus gerardii-dominated), invasive Phragmites australis zones, and unvegetated ponds. Day-and nighttime fluxes were also contrasted in the native marsh zones. N2O fluxes were measured in parallel with CO2 and CH4 fluxes, but were not found to be significant. To test the relationships of CO2 and CH4 fluxes with several native plant metrics, a multivariate nonlinear model was used. Invasive P. australis zones (-7 to -15 μmol CO2m-2s-1) and S. alterniflora low marsh zones (up to -14 μmol CO2m-2s-1) displayed highest average CO2 uptake rates, while those in the native high marsh zone (less than -2 μmol CO2m-2s-1) were much lower. Unvegetated ponds were typically small sources of CO2 to the atmosphere (<0.5 μmol CO2m-2s-1). Nighttime emissions of CO2 averaged only 35% of daytime uptake in the low marsh zone, but they exceeded daytime CO2 uptake by up to threefold in the native high marsh zone. Based on modeling, belowground biomass was the plant metric most strongly correlated with CO2 fluxes in native marsh zones, while none of the plant variables correlated significantly with CH4 fluxes. Methane fluxes did not vary between day and night and did not significantly offset CO2 uptake in any vegetated marsh zones based on sustained global warming potential calculations. These findings suggest that attention to spatial zonation as well as expanded measurements and modeling of GHG emissions across greater temporal scales will help to improve accuracy of carbon accounting in coastal marshes.
... In addition to hydroperiod (duration and frequency of tidal flooding), factors that affect plant distribution in salt marshes and other estuarine communities include soil salinity, soil oxygen, nutrient availability, elevation of substrate, concentration of growth inhibitors in the sulfihemist soils, storms, ice-scouring, and land use history (Breeding et al. 1974;Howes et al. 1986). Competitive interaction and biological facilitation between and among species has also been documented (Bertness 1992). Many of these factors and processes are interrelated, but vary along gradients at different rates or in different quantities (Zoltai and Vitt 1995). ...
... Shallow pannes are created by damage to Spartina patens (saltmeadow cordgrass) and other high marsh vegetation from ice erosion or smothering by stranded mats of Spartina alterniflora (smooth cordgrass) (Bertness 1992) and other flood-deposited plant litter or trash. Other processes account for the formation of "pond holes" or deep pools (Redfield 1972). ...
... It is unclear if narrow-leaved cattail is native here or not, although there is a growing body of evidence indicating this taxon occurred on the Northeast coast prior to European settlement (see discussion under "Estuarine Communities" introduction). SOURCES: NHB field surveys; Redfield 1972;Shea et al. 1975;Howes et al. 1986;Bertness 1992;Nichols et al. 2001. • Marsh elder shrubland (S1) GENERAL DESCRIPTION: This rare community is dominated by Iva frutescens (marsh elder)*, one of only two woody species that grows in New Hampshire's salt marshes. ...
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New Hampshire Natural Heritage Bureau and The Nature Conservancy T he New Hampshire Natural Heritage Bureau is located within the NH Department of Resources and Economic Development's Division of Forests and Lands. Primarily an information resource, the bureau finds, tracks, and facilitates the protection of New Hampshire's rare plants and exemplary natural communities. It is not a regulatory agency; instead, the bureau works with landowners and land managers to help them protect New Hampshire's natural heritage and meet their land-use needs. Its mission, as mandated by the Native Plant Protection Act of 1987 (NH RSA 217-A), is to determine protective measures and requirements for the survival of native plant species in the state, to investigate the condition and rarity of plant species, and to distribute information regarding the condition and protection of these species and their habitats. The New Hampshire Natural Heritage Bureau is an excellent source of information on plants and natural communities in New Hampshire, including their ecology and distribution in the state. It maintains the state's only comprehensive database of New Hampshire's exemplary natural communi-ties, exemplary natural community systems, rare plants, and rare animals, including their known locations. Rare wildlife locations are maintained in cooperation with the Nongame and Endangered Wildlife Program at the New Hampshire Fish and Game Department, which has legal authority over all wildlife in the state. The bureau is also a member of the NatureServe network, which connects nearly 80 Natural Heritage Programs throughout the United States, Canada, and several Latin and South American countries. The Nature Conservancy provides ecology staff and other services to the bureau through a cooperative agreement with the state of New Hampshire.
... The distinct zonation of New England salt marshes plants is characterized by monospecific bands of clonal turfs that are determined by a combination of physical stresses and interspecific competition (Nixon 1982, Bertness 1992). This zonation pattern is disrupted in northern New England marshes by large patches of halophytic forbs, called forb pannes (Theodose andRoths 1999, Ewanchuk andBertness 2004). ...
... Most of our understanding of forb patches comes from southern New England marshes, where forb patches are ephemeral features of marshes (Bertness andEllison 1987, Shumway andBertness 1994). Unlike the persistent forb pannes of northern New England, the forbs in these patch are outcompeted by clonal turfs within a few growing seasons (Bertness and Ellison 1987). ...
... These marshes have undergone extensive ditching as a result of farming of salt marsh hay, live-stock grazing, and insect control. As a result, the classic descriptions of New England salt marshes may be largely descriptions of anthropogenically altered marshes, and the lack of forb pannes in southern New England may be an artificial state (Miller and Egler 1950, Redfield 1965, Nixon 1982, Bertness 1992. ...
Article
Areas of high plant diversity, known as forb pannes, characterize many northern New England salt marshes. These pannes are physically harsh habitats where stress-tolerant forbs escape the competitively dominant clonal turfs. In this paper, we experimentally examine the hypothesis that soil waterlogging maintains forb pannes. Experimentally draining pannes led to the replacement of typical panne vegetation by Spartina patens. After four years, S. patens cover increased by greater than 300% in the drained plots, while in adjacent, unmanipulated controls, its cover remained unchanged. In a second experiment, forb panne elevation was manipulated to either increase or decrease soil drainage. After three years elevated plots were dominated by S. patens, whereas lowered plots were dominated by Spartina alterniflora, with reduced forb densities. Our results demonstrate that forb panne communities are the consequence of poor drainage and waterlogged soils that limit the success of competitively dominant clonal turfs and permit the persistence of panne forbs. These results imply that the extensive ditching of New England salt marshes over the past three centuries to increase the value of marshes for livestock grazing, development, and mosquito control has likely eradicated most of these forb panne habitats.
... For instance, though the UAs and PAs of SaEu varied by composite type, they peaked in study area 1 within the 1 October classification (Tables A1c, A2c, A3c and A4c) and within the 30 September classification for study area 2 (Tables A5b, A6b, A7b and A8b). These peaks in accuracy for SaEu correspond with visual observations of when the plants' spectral reflectance transitions in color from green to bright red within our study areas, displaying similar color characteristics as those described by Bertness (1992) [36]. Additionally, though the UAs and PAs for SoSv were relatively poor for the RGB (Tables A1a-d and A5a-c) and RGN (Tables A2a-d and A6a-c) composites across all the dates, these accuracies increased within the RGBD (Tables A3a-d and A7a-c) and RGND (Tables A4a-d and A8a-c) classifications across all the dates. ...
... For instance, though the UAs and PAs of SaEu varied by composite type, they peaked in study area 1 within the 1 October classification (Tables A1c, A2c, A3c and A4c) and within the 30 September classification for study area 2 (Tables A5b, A6b, A7b and A8b). These peaks in accuracy for SaEu correspond with visual observations of when the plants' spectral reflectance transitions in color from green to bright red within our study areas, displaying similar color characteristics as those described by Bertness (1992) [36]. Additionally, though the UAs and PAs for SoSv were relatively poor for the RGB (Tables A1a-d and A5a-c) and RGN (Tables A2a-d and A6a-c) composites across all the dates, these accuracies increased within the RGBD (Tables A3a-d and A7a-c) and RGND (Tables A4a-d and A8a-c) classifications across all the dates. ...
Article
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New England salt marshes provide many services to humans and the environment, but these landscapes are threatened by drivers such as sea level rise. Mapping the distribution of salt marsh plant species can help resource managers better monitor these ecosystems. Because salt marsh species often have spatial distributions that change over horizontal distances of less than a meter, accurately mapping this type of vegetation requires the use of high-spatial-resolution data. Previous work has proven that unoccupied aerial vehicle (UAV)-acquired imagery can provide this level of spatial resolution. However, despite many advances in remote sensing mapping methods over the last few decades, limited research focuses on which spectral band, elevation layer, and acquisition date combinations produce the most accurate species classification mappings from UAV imagery within salt marsh landscapes. Thus, our work classified and assessed various combinations of these characteristics of UAV imagery for mapping the distribution of plant species within these ecosystems. The results revealed that red, green, and near-infrared camera image band composites produced more accurate image classifications than true-color camera-band composites. The addition of an elevation layer within image composites further improved classification accuracies, particularly between species with similar spectral characteristics, such as two forms of dominant salt marsh cord grasses (Spartina alterniflora) that live at different elevations from each other. Finer assessments of misclassifications between other plant species pairs provided us with additional insights into the dynamics of why classification total accuracies differed between assessed image composites. The results also suggest that seasonality can significantly affect classification accuracies. The methods and findings utilized in this study may provide resource managers with increased precision in detecting otherwise subtle changes in vegetation patterns over time that can inform future management strategies.
... Tidal salt marsh communities along the New England coastline are dominated by salt-tolerant grasses, such as smooth cordgrass and saltmeadow cordgrass (Spartina alterniflora and Spartina patens, respectively). They also contain several detritivore, herbivore, and predator species, of which fiddler crabs (Uca pugnax and Uca pugilator) and purple marsh crabs (Sesarma reticulatum) may have a dominant influence in maintaining salt marsh properties and functions (Bertness, 1992;Moore, 2019). The fiddler crab is a detritivore that alters the landscape through its burrowing behavior and deposit feeding, while the purple marsh crab is a burrowing herbivore that directly consumes marsh vegetation aboveground and belowground (Bertness, 1985;Holdredge et al., 2009;Miller, 1961). ...
... Field experiments were conducted from May to August in 2015 and 2016. This time period covers the S. alterniflora and S. patens growing season when each target consumer species was most active (Bertness, 1991(Bertness, , 1992. Within each study site, experimental blocks comprising groups of three plots were established and randomly placed along the creek-bank edge of the low marsh where smooth cordgrass was the dominant vegetation. ...
Article
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The historical ecological paradigm of wetland ecosystems emphasized the role of physical or “bottom-up” factors in maintaining functions and services. However, recent studies have shown that the loss of predators in coastal salt marshes can lead to a significant reduction in wetland extent due to overgrazing of vegetation by herbivores. Such studies indicate that consumers or “top-down” factors may play a much larger role in the maintenance of wetland ecosystems than was previously thought. The objective of this study was to evaluate whether altering top-down control by manipulating the presence of predators can lead to measurable changes in salt marsh ecosystem properties. Between May and August of 2015 and 2016, we established exclosure and enclosure cages within three New England coastal wetland areas and manipulated the presence of green crab predators to assess how they and their fiddler and purple marsh crab prey affect changes in ecosystem properties. Predator presence was associated with changes in soil nitrogen and aboveground biomass at two of the three field sites, though the magnitude and direction of these effects varied from site to site. Further, path analysis results indicate that across field sites, a combination of bottom-up and top-down factors influenced changes in measured variables. These results challenge the growing consensus that consumers have strong effects, indicating instead that predator impacts may be highly context-dependent.
... Plant height increased but shoot density decreased from barrier island to mainland sites. As has been found previously (Bertness, 1992;Nestler, 1977), this spatial variation was correlated with porewater salinity, with plants shorter in more saline soils (Bertness & Pennings, 2002;Richards et al., 2005). ...
... Both the proportion of stems flowering and the resources allocated to flowering increased with plant height, but the F 50 for flowering also increased with plant height, consistent with general life-history theory. Because of their strong abiotic gradients and low species diversity, saltmarshes have long been a productive study system for studies of community ecology (Bertness, 1992;Chapman, 1974;Pennings & Bertness, 2001); our work suggests that they also offer an excellent model system for studies of plant life history. ...
Article
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Plants adjust their size and reproductive effort in response to numerous selection pressures and constraints. The self‐thinning law describes a well‐known trade‐off between size and density. Plants also trade‐off investment into growth vs. sexual reproduction, as described by life‐history theory. We build on past work on plant allometry and life history by examining both self‐thinning and size‐dependent reproduction in a single plant species, the saltmarsh grass Spartina alterniflora, across a wide range of settings: three landscape positions, two habitats and eight sites, across sixteen years. Plants in different landscape positions and years varied tremendously in size and shoot density. However, all this variation could be explained by a single allometric relationship consistent with the self‐thinning law, but with a lower slope. Flowering was size‐dependent, and the size at which plants had a 50% probability of flowering varied among habitat, sites and years. Plants that were stressed reproduced at a smaller size than plants that were growing under good conditions, and this pattern was consistent among habitat, sites and years. Finally, reproductive biomass and the proportion of shoots flowering increased with increasing vegetative size (plant height or shoot biomass). Combining these two patterns, S. alterniflora plants growing high density are small and reproduce at a smaller size than large plants growing at low density. Although there is tremendous spatial and temporal variation in S. alterniflora growth and reproductive patterns, all this variation can be understood as resulting from two simple allometric trade‐offs. Because saltmarsh plants often occur in monospecific stands, they may serve as simple, model systems for studies of plant life history. A free Plain Language Summary can be found within the Supporting Information of this article.
... Most studies of goose herbivory in subarctic systems have concentrated on relatively homogeneous "grazing lawns," but in many other communities, geese are highly selective foragers (Sedinger and Raveling 1984, Prevett et al. 1985, Prins and Ydenberg 1985, Thomas and Prevett 1986, and their preferred forage species are not always dominant. Recently, numerous studies have shown that competition and facilitation play a major role in the structuring of saltmarsh communities (Snow and Vince 1984, Bertness and Ellison 1987, Ellison 1987, Bertness 1992, Pennings and Callaway 1992, Bertness and Shumway 1993, Bertness and Hacker 1994, Castellanos et al. 1994), but it is not well understood how herbivory, abiotic factors, and interspecific interactions combine to affect establishment and growth of individual saltmarsh plants. ...
... As was found in work on a temperate salt marsh on the east coast of the Unites States, interactions between plant species in the slough levee community range from positive to negative, depending on conditions. Neighboring plants can act as competitors, but they can also have positive effects by buffering harsh physical conditions (Bertness andShumway 1993, Bertness andHacker 1994), or, as in our case, reducing levels of herbivory. ...
Article
Herbivores may affect plants by removing biomass, altering competitive interactions, and altering the abiotic environment. Changes in the size and quality of forage species and in species composition as a result of herbivory, in turn, affect future herbivory. We investigated the direct and indirect effects of herbivory by Brant Geese (Branta bernicla nigricans) on Triglochin palustris (arrowgrass) in a subarctic salt marsh in southwestern Alaska. In the first experiment, we compared arrowgrass in exclosed plots, unexclosed plots with feces removed, and control plots. In the second experiment, we used a full-factorial design to examine the effects of clipping arrowgrass, clipping neighboring plants, depositing goose feces, and their interactions on arrowgrass size and biomass allocation. In the third experiment, we placed hand-reared goslings on premanipulated plots from the second experiment to examine the effects of arrowgrass size, density, and species composition on the probability of an individual arrowgrass plant being grazed. For unclipped plants, feces deposition resulted in reduced bulb mass, reduced percentage of biomass in bulb and roots, and increased percentage of biomass in leaves, whereas feces deposition had no effect on clipped plants. Clipping neighbors resulted in increased arrowgrass root and stolon mass only for unclipped plants. Feces deposition resulted in increased vegetative reproduction when neighbors were clipped, but had no effect on vegetative reproduction when neighbors were not clipped. Plants in exclosed plots were larger, had greater allocation to leaves, had higher concentrations of C and N, and were more likely to flower than were plants in unexclosed plots. These results indicate an increase in competition for light with neighbor plants under feces deposition, which may be ameliorated by biomass removal of neighbors. Our results predict that an increase in grazing pressure is not necessarily detrimental to arrowgrass, provided that it is accompanied by increases in consumption of neighbor plants. The number of arrowgrass plants completely removed was not related to arrowgrass density, but the number of plants partially grazed increased with arrowgrass density. The probability that an individual arrowgrass plant would be grazed was negatively related to biomass or percent cover of several other species (Potentilla egedei, Chrysanthemum arcticum, Carex spp., Salix spp.). These results suggest that some neighbor species may provide a measure of protection (associational refuge) from herbivory, and that an increase in grazing intensity may have a strong negative effect on arrowgrass populations by reducing this protection and through an increased likelihood of consumption of the arrowgrass remaining after neighbors are removed. We conclude that the way in which we view neighboring plants (as competitors or potential protectors) affects our predictions regarding the effects of changing herbivore populations. Feedbacks from the plant community to herbivores following grazing should be included in studies that aim to extrapolate to the population level the effects of herbivory on individuals.
... There is an inverse relationship between a plant's competitive ability and its stress tolerance. Species with stronger competitive abilities occupy less stressful areas, while those with weaker abilities are confined to more stressful zones, such as areas with high salt concentration and oxygen depletion (Bertness, 1992;Pennings and Bertness, 2001). ...
... Both Phragmites and Spartina belong to the grass family (Poaceae) but are structurally similar to native sedges (Cyperaceae) and can have higher CH 4 concentrations in the lacunae (aerenchyma) of their culms than other grasses in their native ranges (Tong et al., 2012). Their aerenchyma facilitate the release of oxygen and exudates into deep soil layers, as well as transport of GHG from those deep layers (Bertness, 1992;Moseman-Valtierra et al., 2016). ...
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Societal Impact Statement The invasive species S. alterniflora and P. australis are fast growing coastal wetland plants sequestering large amounts of carbon in the soil and protect coastlines against erosion and storm surges. In this global analysis, we found that Spartina and Phragmites increase methane but not nitrous oxide emissions, with Phragmites having a lesser effect. The impact of the invasive species on emissions differed greatly among different types of native plant groups, providing valuable information to managers and policymakers during coastal wetland planning and restoration efforts. Further, our estimated net emissions per wetland plant group facilitate regional and national blue carbon estimates. Summary Globally, Spartina alterniflora and Phragmites australis are among the most pervasive invasive plants in coastal wetland ecosystems. Both species sequester large amounts of atmospheric carbon dioxide (CO2) and biogenic carbon in soils but also support production and emission of methane (CH4). In this study, we investigated the magnitude of their net greenhouse gas (GHG) release from invaded and non‐invaded habitats. We conducted a meta‐analysis of GHG fluxes associated with these two species and related soil carbon content and plant biomass in invaded coastal wetlands. Our results show that both invasive species increase CH4 fluxes compared to uninvaded coastal wetlands, but they do not significantly affect CO2 and N2O fluxes. The magnitude of emissions from Spartina and Phragmites differs among native habitats. GHG fluxes, soil carbon and plant biomass of Spartina‐invaded habitats were highest compared to uninvaded mudflats and succulent forb‐dominated wetlands, while being lower compared to uninvaded mangroves (except for CH4). This meta‐analysis highlights the important role of individual plant traits as drivers of change by invasive species on plant‐mediated carbon cycles.
... If Lepidium is indeed reducing soil salinity, this could put Cirsium and other native brackish marsh species at a disadvantage, as salinity tolerance can come with the tradeoff of reduced competitive ability (Bertness 1992;Pennings and Bertness 2001). Furthermore, brackish marsh plant community composition shifts during periods of higher and lower rainfall, with more saline periods favoring Cirsium (USFWS 2013). ...
Article
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Invasive species exert disproportionate impacts in wetlands and pose particular challenges for rare species persisting at small spatial scales. In the urbanized San Francisco Estuary (SFE), which contains 90% of California’s remaining coastal wetlands, invasive and rare species often co-occur. One narrow endemic taxon, the federally listed Suisun thistle ( Cirsium hydrophilum var. hydrophilum ) is restricted to two or three locations where the invasive perennial pepperweed ( Lepidium latifolium ) has an increasing presence. Perennial pepperweed has invaded salt, brackish, and freshwater wetlands around the SFE, leading to high management concern. In this study, we investigated how perennial pepperweed may contribute to further rarity of the Suisun thistle, by conducting a removal experiment and surveying soil-plant relationships. Removing pepperweed led to a doubling of native species relative cover and an increase in native species richness by an average of one species per plot, positive effects on Suisun thistle cover, number, and reproductive output, and shifts in soil properties. Combined with survey data inside and outside of pepperweed stands, we conclude that pepperweed competes with Suisun thistle via competition for space, nutrients, and light, interferes with the Suisun thistle’s reproductive success, and alters brackish marsh soil physicochemical characteristics to further favor pepperweed. We recommend local control of pepperweed to prevent further loss of Suisun thistle. Further, the wide range of mechanisms by which this invasion may proceed if unchecked should be considered in other settings where rare or uncommon species are at risk from invaders.
... alpini and A. portulacoides have greater uptake capacity at lower values. One explanation for the segregation of A. macrostachyum toward the inner zone could be that this species is displaced to the more physically stressful habitat by the other two competitive dominant species as a trade-off between stress tolerance and competitive ability, observed in other saltmarsh plant communities (Bertness, 1992;Pennings and Bertness, 2001;Pennings et al., 2005). However, the zonation in Palmones cannot entirely be explained by that hypothesis, probably because of the lack of a clear gradient in physical stress across the marsh (Costa et al., 2003), at least in terms of salinity. ...
Article
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In Southern European estuaries and associated salt marshes, the anthropogenic nutrient inputs, together with longer drought periods, are leading to increasing eutrophication and salinization of these coastal ecosystems. In this study, uptake kinetics of ammonium, nitrate, and phosphate by three common plants in Palmones salt marsh (Southern Spain), Sarcocornia perennis ssp. alpini, Atriplex portulacoides, and Arthrocnemum macrostachyum were measured in hydroponic cultures. We also determined how these uptakes could be modified by increasing salinity, adding NaCl to the incubation medium (from 170 to 1,025 mM). Kinetic parameters are analyzed to understand the competition of the three species for nutrient resources under realistic most frequent concentrations in the salt marsh. These results may also be useful to predict the possible changes in the community composition and distribution if trends in environmental changes persist. Atriplex portulacoides showed the highest Vmax for ammonium, the most abundant nutrient in the salt marsh, while the highest affinity for this nutrient was observed in A. macrostachyum. Maximum uptake rates for nitrate were much lower than for ammonium, without significant differences among species. The highest Vmax value for phosphate was observed in A. macrostachyum, whereas A. portulacoides presented the highest affinity for this nutrient. High salinity drastically affected the physiological response of these species, decreasing nutrient uptake. Sarcocornia perennis ssp. alpini and A. macrostachyum were not affected by salinity up to 510 mM NaCl, whereas A. portulacoides notably decreased its uptake capacity at 427 mM and even withered at 1,025 mM NaCl. At current most frequent concentrations of ammonium and phosphate in the salt marsh, S. perennis ssp. alpini is the most favored species, from the nutritional point of view. However, A. portulacoides could enhance its presence if the increasing ammonium load continues, although a simultaneous salinization would negatively affect its nutritional physiology.
... Salt marshes are highly diverse, but are also constantly changing due to human and natural influences (Redfield, 1972). North American marshes are very productive and have been the subject of many studies (Nicol, 1936;Redfield, 1972;Jacobson & Jacobson Jr., 1989;Bertness, 1992). There are however very few natural and undisturbed marshes remaining in North America due to human exploitation, invasive species, and different types of degradation, including pollution (Zedler et al., 2004;Bromberg Gedan et al., 2009). ...
Chapter
Mangrove ecosystems provide invaluable protection from climate change impacts and create environments in which communities can build coastal resilience. They are situated at the interface of saltwater and freshwater sources, where the stable flow of sediment and freshwater allows mangrove forests and associated livelihoods to thrive. One of the largest mangrove forests in Southeast Asia is located in Peam Krasaop Wildlife Sanctuary of Koh Kong Province in Cambodia. It is supported by a 4 km The community of Koh Kapik relies on surrounding mangroves for protection from coastal hazards. However, as the barrier beach to the mangroves retreats landwards, fishing villages are becoming increasingly vulnerable to coastal hazards. River sand mining and sea level rise are likely responsible. Forest conservation, initiated by IUCN, would improve the consistent flow of freshwater and sediments from the upstream rivers to the ocean, thereby reducing barrier beach migration and coastal disaster risks. This case study highlights the importance of protected area management that accounts for hydrological connectivity from the upstream watershed to the coast, and it provides further recommendations to protect mangrove-dependent livelihoods from coastal hazards. This research proposes river management strategies that will reduce barrier beach migration and build coastal resilience. It establishes priority zones for rehabilitation on the barrier beach, based on barrier beach migration rates. Coastal features, including spits and un-vegetated beaches within these priority zones are targeted for intervention. Re-vegetation with local plant species will prevent further landward migration of the barrier beach and protect livelihoods. During a provincial workshop and meeting with national government representatives the use of these strategies was discussed. This improved understanding of the highly connected sediment dynamics, coupled with rehabilitation and erosion prevention strategies, offers a pathway to build greater coastal resilience in Peam Krasaop Wildlife Sanctuary. Similar socioecological systems exist throughout the tropics, and lessons learnt from this case study can therefore be examined for application to other mangrove-dependent communities.
... We obtained UTM coordinates and the total area sampled from 1995 Natural Resources Conservation Service/U.S. Geological Survey digital orthophotographs and map data (NAD 27) from Rhode Island Geographic Information System (RIGIS) (August et al. 1995). Dominant vegetation types across study sites were salt meadow (Spartina patens, Juncus gerardii, and Distichlis spicata), salt-marsh cordgrass (Spartina alterniflora), common reed (Phragmites australis), and hightide bush (Iva frutescens) (Bertness 1992). Galilee was dominated by extensive stands of common reed, due to a restricted tidal regime. ...
Article
We investigated site fidelity and apparent survival in a promiscuous population of Saltmarsh Sharp-tailed Sparrows (Ammodramus caudacutus) in southern Rhode Island. Based on capture–recapture histories of 446 color-banded sparrows studied from 1993 to 1998 at our primary study site, Galilee, we observed significant variation in apparent survival rates among years, but not between sexes. Return rates of adult males (37.6%) and females (35.6%) were not significantly different during any year. Juveniles exhibited high return rates, ranging from 0 to 44%, with males (61% of returns) more likely to return than females (35%). In addition, we monitored movements of 404 color-banded sparrows at nine satellite marshes in 1997 and 1998, which supported our findings at Galilee and documented intermarsh movements by 10% of all banded birds. Lack of gender-bias in adult dispersal and strong natal philopatry of sparrows in Rhode Island occurs regularly among passerines possessing a variety of mating systems. Despite emancipation from parental and resource defense duties, adult male Saltmarsh Sharp-tailed Sparrows exhibited apparent survival rates similar to adult females. Availability of high-quality breeding habitat, which is patchy and saturated, may be the most important factor limiting dispersal for Saltmarsh Sharp-tailed Sparrows in Rhode Island.
... Salt marshes are highly diverse, but are also constantly changing due to human and natural influences (Redfield, 1972). North American marshes are very productive and have been the subject of many studies (Nicol, 1936;Redfield, 1972;Jacobson & Jacobson Jr., 1989;Bertness, 1992). There are however very few natural and undisturbed marshes remaining in North America due to human exploitation, invasive species, and different types of degradation, including pollution (Zedler et al., 2004;Bromberg Gedan et al., 2009). ...
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About IUCN IUCN, International Union for Conservation of Nature, helps the world find pragmatic solutions to our most pressing environment and development challenges. IUCN's work focuses on valuing and conserving nature, ensuring effective and equitable governance of its use, and deploying nature-based solutions to global challenges in climate, food and development. IUCN supports scientific research, manages field projects all over the world, and brings governments, NGOs, the UN and companies together to develop policy, laws and best practice.
... Plant individuals adjust themselves phenologically, physiologically or morphologically to stress. Negative relation between competitive and stress tolerance is one of the most important factor that effecting the distributing of plant distribution and community structuring [2,3]. Plant characteristics such as life form and strategy use both for classification of communities, estimate the ecosystem functions and explanation of succession process [4,5,6,7,8]. ...
Conference Paper
Introduction: Wetland are very productive and stressful environment. Plant individuals adjust themselves phenologically, physiologically or morphologically to stress. Negative relation between competitive and stress tolerance is one of the most important factor that effecting the distributing of plant distribution and community structuring. In this study, we aimed to determine distribution of CSR (competitive, stress-tolerant, ruderal) strategy types in floodplain forest in Aksaz-Karagöl Wetland. Material and Methods: The present study was carried out between 2015-2017 years. Plant taxa, CSR strategy types and cover percentage of each taxa were identified. Specific leaf area (SLA), canopy height, dry matter content, leaf dry weight, lateral spread, flowering initiation and flowering period were used to determine CSR types. For the field measurements, at least ten individuals of each species were marked, while three individuals were used for leaf characters. Results: 85 plant taxa and 14 different CSR strategy types were identified in floodplain forest. The most abundant CSR types were C, C/CS, CR and C/CR. The cover percentage of these types were 107.7%, 43.1%, 36.9% and 13.3%, respectively. Discussion: According to results, competitive strategies are abundant in floodplain forest. On the other hand, representing of ruderal strategies after competitive ones shows low disturbance in the forest. Presence of the other strategy types could be mean that the forest has functional diversity. Acknowledgement: This study was supported by TUBITAK (The Scientific and Technological Research Council of Turkey, project no. 114O796). Keywords: Floodplain forest, CSR strategies, Aksaz-Karagöl Wetland, Sinop
... Salt marshes are highly diverse, but are also constantly changing due to human and natural influences (Redfield, 1972). North American marshes are very productive and have been the subject of many studies (Nicol, 1936; Redfield, 1972; Jacobson & Jacobson Jr., 1989; Bertness, 1992). There are however very few natural and undisturbed marshes remaining in North America due to human exploitation, invasive species, and different types of degradation, including pollution (Zedler et al., 2004; Bromberg Gedan et al., 2009Figure 1), it is part of New Brunswick's Lowlands. ...
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As a protected landscape, Mount Mantalingahan’s importance lies in it being a Key Biodiversity Area (KBA) and one of ten Alliance for Zero Extinction (AZE) sites in the Philippines. However, prior to its declaration as a protected landscape, its forest area was not only in danger of mining activities but also of several hazards such as flooding and landslides. The declaration of Mount Mantalingahan as a protected landscape, along with its associated livelihood programmes for the mountain’s inhabitants, allowed for participatory activities that contributed to reduction of flooding and landslide risks in addition to livelihood improvements in three out of five municipalities that are included in the protected landscape. Disaster risk reduction in protected landscapes is best pursued in conjunction with conservation and development objectives. Through several conservation agreements with Conservation International-Philippines (CI-P), local communities in the Mount Mantalingahan Protected Landscape (MMPL) restored and conserved watersheds and, in the process, developed soft skills in managing community forestry enterprises and local water cooperatives.
... Ecologists have historically emphasized the role of physical factors in determining the community structure of saltmarsh plants (Nixon 1982), but recent work has demonstrated that competitive processes are also important (Snow and Vince 1984, Bertness and Ellison 1987, Bertness 1991a, b, Pennings and Callaway 1992, Levine et al. 1998). Finally, salt marshes are nitrogen poor Teal 1974, Valiela et al. 1985) yet highly productive (Bertness 1992) and thus are potentially sensitive to changes in nutrient availability. ...
Article
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Although a great deal of research has focused on the effects of nutrient supply on plant competition, few studies have explored how these processes interact with non-resource factors to determine community-level patterns. This study examined how resource competition interacts with physical stress to structure salt-marsh plant communities across a natural gradient in tidal stress. First, nutrient additions at naturally,occurring species borders at zonal and patch boundaries in two Rhode Island (USA) marshes revealed that competitive outcomes were typically reversed when nutrients were abundant. These results, which are consistent with earlier findings in a third southern New England marsh, suggest that a nutrient-dependent competitive hierarchy is a general characteristic of salt marshes in this region. To test whether these shifts in competitive outcomes occur only at naturally occurring species borders or can lead to more significant shifts in zonation patterns, lower marsh species were transplanted into the matrix of each zonal species at higher tidal elevations, and the outcomes of plant competition in fertilized plots and unfertilized plots were compared. Results of this experiment indicate that nutrient effects on the competitive relations of marsh plants were independent of where the interactions took place along the tidal gradient. The stress-tolerant species were consistently the best competitors in fertilized treatments, showing that an increase in nutrient availability can lead to drastic shifts in the distributions of plants across marshes. Finally, a third experiment examined the interaction between nutrient supply and the aboveground and belowground components of plant competition using a reciprocal transplant design coupled with nutrient-addition and neighbor-removal treatments. Results suggest that. competition is primarily belowground under ambient marsh conditions but is aboveground at high nutrient levels. Thus the mechanism underlying the nutrient-dependent competitive hierarchy, may be driven by a trade-off between belowground and aboveground competitive abilities, although the potential interaction between above- and belowground effects was not examined. Together, the results of these experiments suggest that nutrient supplies may significantly affect the competitive dynamics between salt-marsh perennials and their resultant zonation.. across an environmental gradient in tidal stress. The result that stress tolerators can be dominant competitors is not predicted by any current model of plant competition and must be considered in future empirical and theoretical studies.
... Salt marshes are highly diverse, but are also constantly changing due to human and natural influences (Redfield, 1972). North American marshes are very productive and have been the subject of many studies (Nicol, 1936; Redfield, 1972; Jacobson & Jacobson Jr., 1989; Bertness, 1992). There are however very few natural and undisturbed marshes remaining in North America due to human exploitation, invasive species, and different types of degradation, including pollution (Zedler et al., 2004; Bromberg Gedan et al., 2009Figure 1), it is part of New Brunswick's Lowlands. ...
... Where the tall cordgrass meets the water's edge, the mud is home to densely packed beds of ribbed mussels, and around the plants' roots, one can find small holes that form the openings to fiddler crab burrows. Moving away from the water, at the edge of the border marked by the high-tide line, the cordgrass is short, less than 30 cm tall (Bertness, 1992). ...
... New England salt marsh landscapes have been typified by a general zonation of low-marsh, high-marsh, and upland-transition plant patches determined by tidal range and duration, plant tolerances to inundation, and related physical and chemical conditions (e.g., salinity), and biotic interactions among the plants and animals inhabiting the marsh (Bertness 1985(Bertness , 1991(Bertness , 1992Bertness and Ellison 1987;Niering and Warren 1980). Local disturbances generate open patches within these zones that go through successional changes, adding to the spatial variation of plant community structure. ...
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The spatial distribution of the fiddler crab Uca pugnax (Atlantic Marsh Fiddler Crab) in relation to salt marsh patch structure was investigated along the central Connecticut coast of Long Island Sound. Salt marsh landscape structure at the study sites exhibit characteristics consistent with changes noted in other systems along the US Atlantic coast over the last several decades, including significant seaward erosion, encroachment of low-marsh plants into high marsh, changing composition of high-marsh plant patch structure, and marsh dieback and drowning. Our objective was to determine whether the spatial patterns of U. pugnax inhabiting these systems differed from those previously reported for southern New England in light of these characteristics. Densities of crab burrows were highest in low-marsh patches of Spartina alterniflora (Atlantic Smooth Cordgrass) and unvegetated muds along tidal creek banks and mosquito ditches. Seaward-eroding low-marsh areas were generally devoid of live crabs and burrows. Crab-burrow densities varied across the complex patch mosaics in high-marsh areas. Burrow densities were generally low in the extensive short S. alterniflora patches that comprised much of the high-marsh area at several sites. However, high burrow densities, equivalent to low-marsh densities, were found in certain high-marsh patch types and upland transition zones. These included patches of Spartina patens (Marsh Hay Cordgrass), Distichils Spicata (Desert Salt Grass), and mixes of these, and particularly in S. patens patches wholly or partly comprised of hummocks of vegetation surrounded by bare sediment. At several sites, burrow densities were high in upland transition zone patches of Phragmites australis (Common Reed). As such, crab-burrow distributions were highly variable at local, within-marsh system spatial scales. Live U. pugnax were found regularly in all patch types on all marshes. Our results indicate a much broader distribution of U. pugnax at relatively high densities across southern New England marsh landscapes than previously reported. This finding may represent a case of habitat expansion in response to salt marsh change, likely due to sea-level rise and other factors, creating high-marsh habitats in a variety of patch types that can support resident populations of fiddler crabs. Such an expansion of a dominant salt marsh species, which can significantly affect ecosystem dynamics, may potentially increase the complexity of current salt marsh change patterns and dynamics along southern New England coastlines.
... Where the tall cordgrass meets the water's edge, the mud is home to densely packed beds of ribbed mussels, and around the plants' roots, one can fi nd small holes that form the openings to fi ddler crab burrows. Moving away from the water, at the edge of the border marked by the high-tide line, the cordgrass is short, less than 30 cm tall (Bertness, 1992). ...
... Tidal marshes are highly productive with large amounts of new plant tissue produced each year (Niering and Warren, 1980;Bertness, 1992). Most of the primary production dies and is converted to detritus which supports often dense populations of macroinvertebrates (Subrahamanyam et al., 1976;Price, 1980Fell et al., 1982. ...
Article
Reed grass (Phragmites australis (Cav.) Trin. ex Steud.) has invaded large areas of tidal marsh along the lower Connecticut River and often occurs as a monoculture. Tidal marsh invertebrates (snails, amphipods and isopods) were common to abundant in reed grass-dominated regions, as well as in areas covered by typical tidal marsh vegetation at four sampling stations set up along the salinity gradient. This finding suggests that reed grass marshes provide suitable physical habitat and usable food resources for these semiaquatic detritus/algae feeders. Mummichogs (Fundulus heteroclitus L.) were caught on the high marsh during daylight high tides using Breder traps and an analysis of their gut contents was made. When daylight tides were high enough to cover the marsh surface, mummichogs moved up onto the marsh and fed extensively on marsh invertebrates, both in reed grass marshes and reed grass-free marshes. Such foraging appears to represent a direct trophic link between the marshes and adjacent estuarine waters. Even when tides were not high enough to flood the marsh surface, mummichogs moved into the tidal creeks that course through reed grass marshes and largely reed grass-free marshes and foraged there. With respect to macroinvertebrate populations and mummichog foraging, the reed grass marshes appear to be functioning in essentially the same ways as nearby marshes not invaded by this plant, at least in the short term.
... Tidal submergence is a complex measure that serves as the primary control of the elevational ranges of tidal marsh plant species (Hinde 1954;Atwater and others 1979;Macdonald 1988; Byrne and others 2001; Watson and others submitted). Plant functional traits that convey stress-avoidance or stress-tolerance ability combine with competitive and facilitative interactions among plant species to influence estuarine plant species presence and abundance across environmental gradients (Keddy 1990;Bertness 1992;Pennings and Bertness 2001;Grewell and others 2007;Grewell 2008a). At a local scale, the environmental heterogeneity associated with hydrogeomorphic complexity combines with past land use and location to support distinct plant communities and assemblages. ...
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The Rush Ranch Open Space Preserve (Rush Ranch) is located at the northwestern edge of the Potrero Hills and includes the largest remaining undiked tidal wetland within the Suisun Marsh region of the San Francisco Estuary. The brackish tidal wetlands grade into the transitional vegetation and undeveloped grasslands of the Potrero Hills, and we describe diverse vegetation that reflects the estuarine position, land use history, and hydrogeomorphic complexity of the site. We present a useful framework for future study of vegetation at this San Francisco Bay National Estuarine Research Reserve site. Rush Ranch includes four major estuarine geomorphic units that are widely distributed in the region and support vegetation: subtidal channel beds, fringing tidal marsh, tidal marsh plain and tidal marsh–terrestrial ecotone. These are distinguished by small variations in hydrology and elevation, as noted and described through field observations and historic vegetation-mapping data. We discuss vegetation within each of these landforms, considering each vegetation community as a function of changing physical environment and biological interactions. Past land use and exotic plant species invasions have substantially altered Rush Ranch's tidal marsh vegetation patterns. Our results indicate 27% of the current estuarine wetland-associated flora at Rush Ranch are exotic species, and several are highly invasive. Despite these influences, Rush Ranch's position in the landscape provides important and increasingly rare habitat linkages between the tidal marsh and upland grasslands, which allows great potential for restoration and enhancement. We present a detailed flora and vegetation analysis by hydrogeomorphic setting to provide an ecological framework for future monitoring, research, and adaptive conservation management at Rush Ranch.
... The relative importance of salinity as a component of increased flooding is more difficult to assess. Salinities between 30 and 40 ppt will impart a certain level of stress on S. patens (Bertness, 1992;Ewing et al., 1995) but not cause mortality. In fact, S. patens is capable of surviving salinities between 60 and 93 ppt (Crain et al., 2004;Hester, Mendelssohn, and McKee, 1996). ...
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Salt marsh dieback in different regions of the United States exhibits considerable variability in symptoms, processes, and theoretical or proven causes. On Cape Cod (Massachusetts), where losses within the low-marsh zone (elevations below mean high tide, dominated by smooth cordgrass [Spartina alterniflora Loisel.]) have been particularly severe, recent studies suggest that intense grazing pressure from increased abundances of a native, herbivorous, purple marsh crab (Sesarma reticulatum) is to blame. Low-marsh dieback is spatially heterogeneous because it is closely related to the distribution of the crabs' preferred substrate (peat vs. sand or mud). However, vegetation losses have also occurred in the high marsh, which is comprised of mainly saltmeadow cordgrass (Spartina patens [Aiton] Muhl). In contrast to the low marsh, high-marsh losses consistently occur along the seaward-most edge of this zone, suggesting a link with hydrology (flooding frequency). In this study, we attempted to determine the relative contribution of environmental factors and crab herbivory to high-marsh dieback. To do this, we (1) characterized tidal regimes in dieback vs. healthy areas, (2) assessed the extent of herbivory on S. patens using crab-exclosure cages, (3) documented the ability of S. patens to recover from simulated grazing (clipping) in different marshes and in different areas of individual marshes, and (4) estimated densities of S. reticulatum in two high-marsh dieback areas. The results indicate that S. patens losses are likely the result of a combination of Stressors. Flooding frequency and salinities are higher in dieback areas, which impart a higher level of physiological stress. Plants growing there also seem to have a much-reduced capacity to recover from both simulated and actual grazing by the herbivorous crab, S. reticulatum. Continued losses of high-marsh vegetation could eliminate this community from coastal wetlands on Cape Cod, Massachusetts.
... The fact that both trait and genotypic diversity were important for stem density and spatial spread in this experiment is consistent with prior findings that S. alterniflora intraspecific diversity can be important for density and spatial spread during the colonization stage (Wang et al. 2012). Abiotic stress from inundation and salinity is high in sparsely vegetated areas (Bertness 1992;Pennings & Bertness 2001), and these strong abiotic forces could have enhanced (c.f., Reusch et al. 2005) or overwhelmed (c.f., Johnson et al. 2008) the effects of genotypic diversity. The relative importance of genotypic and trait diversity in colonizing versus established marshes remains unclear. ...
Article
Intraspecific diversity can have important effects on population, community and ecosystem processes, yet we have little understanding of the relative importance of genetic‐ versus trait‐based measures of intraspecific diversity. I conducted a manipulative field experiment of plant ( Spartina alterniflora ) genotypic diversity and trait diversity to examine their independent and interactive effects on plant performance and community structure. I focused on variation within and among genotypes in plant stem height, a trait that varies substantially across environmental gradients and can be an important predictor of plant competition intensity. Trait and genotypic diversity interactively affected multiple metrics of plant performance. Both stem density and spatial spread increased with genotypic diversity in the low trait diversity combinations, yet there were negligible to weak negative effects in the high trait diversity treatments. Spartina alterniflora percentage cover also varied with genotypic and trait diversity, but not in a clear linear pattern. There were no effects of trait or genotypic diversity on associated macrofauna above‐ground, yet they interactively affected below‐ground measures. Infaunal abundance and sediment oxygen availability mirrored the idiosyncratic response of plant percentage cover. Despite the interactive effects of genotypic and trait diversity, high trait diversity consistently increased plant performance in genotypic monoculture. Synthesis . The effects of intraspecific plant trait diversity on a range of plant and community responses in this study reinforce the premise that functional differences underlie ecological effects of genetic diversity and suggest that readily measured trait variance may serve as a valuable predictor of plant performance.
... The reference salt marsh is an undisturbed estuarine, emergent wetland dominated by Spartim alternifora (saltwater cord grass) and Spartina patens (salt meadow cordgrass) (Miller and Egler 1950, Niering and Warren 1980, Nixon 1982, Teal 1986, Bertness 1992. The former, growing l-2 meters in height, characterizes the low marsh and it is flooded by every tidal cycle. ...
... In a salt marsh, the physical arrangement (spatial pattern) of flora and fauna (LaSalle et al. 1991;Levine 1998) is dependent on an organism's tolerance (Cowardin et al. 1979;Chabreck 1988;Fahrig 1997;Costa et al. 2003;Lindig-Cisneros et al. 2003) to periodic flooding (Zeff 1999) and hydrological gradients (Bolton 1991;Hughes et al. 1998, Kuhn et al. 1999) associated with changes in salinity, nutrients, oxygen availability and temperatures (Craft et al. 1988;Cai and Wang 1998). Salt marsh environmental gradients are complex and extremely variable (Chapman 1973;Stout et al. 1982;Bertness 1992;Pennings and Bertness 2001;Wallington et al. 2005;Benincá et al. 2008), where a slight change can alter the dominant vegetation (Chapman 1976;Brinson and Christian 1999;Mallin and Corbett 2006) and corresponding animal habitats (Adam 1990;Reed and Rozas 1995;Wilcox and Meeker 1995;Chambers et al. 1999;Angradi et al. 2001). ...
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Ecosystem structure and function in a Juncus roemerianus dominated marsh in coastal Mississippi was investigated using remote sensing techniques. Rate of change in land cover types were computed from historical aerial photography (1940 to 2006) of the study area located in Kreole, MS. Baseline biodiversity and vegetation coverage were determined from in situ line intercept vegetation analyses. Post-classification difference maps for intervals between image time periods and baseline parameters were compared using 2006 vegetation transects and a 1 m resolution Digital Ortho Quarter Quadrangle (DOQQ) image as ground-reference. The ancillary photographs and digital imagery were rectified, digitized and interpreted from both analog and digital file formats using a combination of geospatial techniques. A Gaussian normalization technique provided a minimum standard deviation in pixel brightness among 1940, 1985 and 2006 images as compared to other image normalization techniques. Additional investigations were made from images with dates significant to Hurricane Elena (1985) and xxv Hurricane Katrina (2005) storm events in coastal Mississippi. Data collected from Mahalanobis distance supervised image classification and simple value difference maps demonstrated that change in marsh structure did occur between pre and post-storms at the study area in Mississippi. A classification error matrix showed accuracies ranging from 46.80% in the 1940 classification to 91.96% in the 2006 ground reference. The supervised post classification percent change of natural marsh for the Hurricane Elena (1985) imagery was + 5.25% Juncus roemerianus marsh, +2.47% pine hummock, +0.91% open-water, -7.14% salt panne, and +0.34% unclassified. The Hurricane Katrina (January 2004-March 2006) supervised post classification percent change was +13.62% Juncus roemerianus marsh, - 13.3230% pine hummock, -2.90% open-water, +2.61% salt panne, and 0.0% unclassified. The percent change difference map for Hurricane Elena (natural) was 0%, 10.81%, 88.85%, and 0.34% respectfully with a mean of 2.8952% and standard deviation of 1.0683% across all classes. The Hurricane Katrina percent change difference was 0%, 11.68%, 88.32%, and 0% respectively with a mean of 2.8832% and standard deviation of 0.3212 %. The overall pixel change in pre and post storm images from Hurricane Elena were 10.34% of the pixels (2811 m2) and 11.68 % (3175 m2) for Hurricane Katrina.
... Since species and populations are the essential currency of applied ecology and the grist of evolution, future research is needed to bridge this gap from the qualitative to the quantitative. Furthermore, innovations to our understanding of the generation of population and even community dynamics can come from studies relating individual behavioral or physiological responses to environmental forcing: rarely do such studies make the connections between the individual and the population, despite a potential for enhancing predictive capacity by uncovering the underlying mechanisms for population and community change (Bertness 1992, Wootton 1993, Micheli 1997. ...
Article
Research in seashore and seafloor communities has contributed immensely to the conceptual growth of ecology. Here we summarize some of the most important findings and discuss needs and opportunities for future work. Disproportionately large numbers of the most influential contributions are derived from studies of rocky shores and coral reefs because aspects of these Systems (accessibility) and of their most common species (sessile or weakly motile, high density, short generation time) make them well suited to manipulative experiments. Foremost among the research contributions from seashore and seafloor systems are increased understanding of (1) competition and consumer-prey interactions, (2) trophic cascades and other indirect species interactions, (3) the evolution of defense and resistance in consumer-prey systems, (4) the importance of propagule transport and recruitment variation to adult populations, (5) the impacts of physical disturbance, and (6) the generation and maintenance of species diversity on ecological time scales. We acknowledge the importance of manipulative experiments in the growth of marine ecology, but question whether a strict adherence to this approach will best serve future needs. Some of the most pressing needs for future knowledge are: (1) documenting the complex influences of spatial and temporal scales on ecological processes, (2) identifying the role of large, mobile predators in marine ecosystems, (3) understanding factors limiting marine autotrophs, (4) integrating historical biology and neontology, and (5) appreciating intersystem linkages. Increased attention to conducting arrays of experiments, taking measurements and observations, and documenting change at larger scales of space and time will provide insights that are unattainable by the commonly used methodological protocols. Novel approaches, including (1) evaluating and managing human disturbance for the joint purpose of conservation and learning, (2) developing stronger ties between scientists working in open-ocean and near-shore systems, and (3) developing collaborative projects among scientists in the academic, governmental, and private sectors are required to understand many of these processes.
... These zones may experience increased inundation and move horizontally in the landscape as relative sea-level rises. The way these zones respond to increased inundation depends on their position in the landscape, slope, and sedimentary regime (Redfield 1972, Stevenson et al. 1985, Bertness 1992, Brinson et al. 1995, Christian et al. 2000. The creekbank either may prograde seaward or erode depending on sediment supply. ...
Article
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Zones in salt marshes can be distinguished by different community and ecosystem properties. As marshes respond to changes in sea level, one might expect alterations in the relative proportions of these zones and, hence, alterations in overall functioning. We used ecological network analysis to assess potential changes in 1 ecosystem function, nitrogen cycling. We constructed nitrogen cycle networks of zones (creekbank, low marsh, and high marsh) for 3 salt marshes on the East Coast of the USA; Great Sippewissett in Massachusetts, Upper Phillips Creek in Virginia, and Sapelo Island in Georgia. The same network structure was applied to all zones, largely using data derived from the literature on the 3 marshes. The factors used to analyze how nitrogen flowed through each zone included how nitrogen imported into the marsh was exported, how imports were related to primary productivity, and how much nitrogen was cycled within the system. Emphasis was placed on identifying patterns across zones that were consistent for all 3 marshes. When precipitation and tidal particulate nitrogen (PN) were the imports, export from active cycling via burial and denitrification significantly increased in importance moving across the marsh from the creekbank to the high marsh. Relative nitrogen cycling also significantly increased from creekbank to high marsh. As the area of the marsh zones decrease or increase in response to sea-level rise, nitrogen dynamics will change as a consequence, If the landscape slope is low allowing the marsh to migrate overland, the high marsh zone will increase in area. Nitrogen cycling as a percentage of total system throughput will increase per unit area averaged over the total marsh. If, however, the marsh stalls because of a steep slope at the upland margin, cycling will decrease on a per unit area basis. If the supply of sediment is great and the marsh progrades toward the sea, nitrogen cycling within the marsh may decrease. Therefore, as relative sea-level rises, the response of a salt marsh's nitrogen cycle will depend on the slope and sediment supply available to the marsh.
Chapter
Salt marshes are highly dynamic and important ecosystems that dampen impacts of coastal storms and are an integral part of tidal wetland systems, which sequester half of all global marine carbon. They are now being threatened due to sea-level rise, decreased sediment influx, and human encroachment. This book provides a comprehensive review of the latest salt marsh science, investigating their functions and how they are responding to stresses through formation of salt pannes and pools, headward erosion of tidal creeks, marsh-edge erosion, ice-fracturing, and ice-rafted sedimentation. Written by experts in marsh ecology, coastal geomorphology, wetland biology, estuarine hydrodynamics, and coastal sedimentation, it provides a multidisciplinary summary of recent advancements in our knowledge of salt marshes. The future of wetlands and potential deterioration of salt marshes is also considered, providing a go-to reference for graduate students and researchers studying these coastal systems, as well as marsh managers and restoration scientists.
Article
The services and functions provided by coastal wetlands are numerous and influenced by factors ranging from climate and tidal regime to ecosystem engineers and anthropogenic modifications. In New England salt marshes, fiddler crabs and purple marsh crabs are cooccurring species that are among the most conspicuous burrowing macroinvertebrates in the region. Both are known to influence salt marsh ecosystem functions through their burrowing and feeding behavior, but the ways in which they regulate specific properties, individually and together, is unclear. Using an ex situ mesocosm study, I manipulated the presence of fiddler crabs and purple marsh crabs in order to evaluate their impact on several soil properties and aboveground biomass. Results show that, contrary to previous studies, the fiddler crab had little impact while the purple marsh crab altered soil quality with positive implications for plant growth. This suggests that the purple marsh crab, known to be a voracious consumer of marsh vegetation, may play a much more nuanced role in the maintenance of plant growth than previously thought. Additional ex situ studies should be done to further delineate the impact of these two species.
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Urbanization and industrial development pressures have seriously impacted coastal ecosystems, including vegetated intertidal and subtidal marine habitats such as barrier strands and associated wetlands and seagrasses. These ecosystems provide a suite of services including carbon storage, pollution and nutrient abatement, soil formation, fisheries support, and flood and storm protection. Emphasis has been placed on vegetated marine habitats that occur immediately adjacent to the Gulf of Mexico, including barrier islands and beaches, salt marshes and mangroves, seagrasses, intertidal and subtidal flats, and reed marshes at the mouth of the Mississippi River. These habitats, their depositional environments, and the ecology of their dominant flora and fauna are described within the context of major marine and terrestrial ecoregions. The information and analysis in this chapter should better enable effective management and restoration of coastal habitats in the Gulf as environmental change continues to alter their structure and function and reshape their associated biotic assemblages.
Chapter
The 1996 controlled flood failed to demonstrate five aspects of its primary vegetation-related management goal of removal of near-shore vegetation. First, when compared to pre-flood measurements, total vegetative cover was reduced only 20% and the areal extent of wetland and woodland/shrubland patches was not significantly different from the previous year when measured 6 months after the high flows. There was an immediate effect in terms of burial of some marshy areas under coarse sand, but most of these recovered within 6 months. Second, the controlled flood consistently affected only the lowest vegetation layer (grasses and herbs). Third, there was some effect on soil seed banks; sites lost roughly 45% of the seeds and 30% of the species richness of the pool of readily germinable seeds in the top 10 cm of the soil. Fourth, the loss of surface organic matter (duff) was significant in only 3 of the 9 sites, the other 6 showed no significant differences between years. There was no significant change across all sites. Finally, although there was no consistent effect on germination site quality in terms of mean soil grain sizes, there was a significant homogenization of substrates within and among sites due mostly to the loss or burial of fine sediments in return current channel settings. As documented in other chapters of this volume, the controlled flood was a success administratively and a successful demonstration of other management goals, especially in moving sediment from the channel bottom to high elevation deposits. Further, the flood was also a success in that it provided a relatively consequence-free opportunity to learn about flood hydrographs and vegetation in this system. Our data and those of others in this volume suggest that had the flows been successful in removing plants and reworking the underlying substrate in wetland patches, the recovery of vegetation would have been slowed considerably by the lack of fine, nutrient-rich sediments.
Article
Now championed as critical habitats for plants, animals, and people because of the environmental service and protection they provide, salt marshes were once considered unproductive wastelands. Salt Marshes, with an emphasis coastal wetlands in the Atlantic and Gulf regions and the San Francisco Bay area, offers readers a wealth of essential information about a variety of flora and fauna, marshes' ecological importance, consequences of human neglect and overdevelopment, and insight into how these wetlands recover.
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Rush Ranch includes the largest remaining tidal marsh within Suisun Marsh of the San Francisco estuary. Estuarine geomorphic units frame its diverse wetland vegetation, influenced by estuarine position, land-use history, and the hydrogeomorphic structure of the site. The geomorphic-vegetation units (subtidal channel beds, fringing tidal marsh, tidal marsh plain, and tidal marsh-terrestrial ecotones) are distinguished by variations in hydrology, substrate, and elevation. We consider the vegetation with each landform as a function of past and modern physical processes and biological interactions. Historical land uses and exotic plant invasions have substantially altered Rush Ranch tidal-marsh vegetation and species diversity. Rush Ranch's landscape position provides important and increasingly rare terrestrial ecotones between the tidal marsh and lowland grasslands, providing potential for estuarine transgression with rising sea level.
Chapter
Coastal wetlands are plant communities at the land-sea interface. Two common types of coastal wetlands are salt marshes and mangrove swamps. Marsh vegetation is typically comprised of grasses and shrubs, and mangrove swamps are dominated by trees. Salt marshes are widespread in cooler temperate latitudes, but most mangrove species cannot tolerate freezing temperatures, so they grow in warmer tropical and subtropical latitudes. Salt marshes and mangroves overlap in some subtropical regions; these areas may undergo shifts in foundation plant species composition in response to climate change. The dynamics and ecological consequences of these shifts are important topics for future research. Plants in coastal wetlands are anatomically and physiologically adapted for abiotic stressors including prolonged inundation, which causes soil anoxia, and high salinity. Salt marshes exhibit predictable zonation patterns, where the distribution of species within a site predictably varies with small changes in elevation. These zonation patterns are driven by species-specific adaptations to abiotic stressors and by interspecific competition. Zonation patterns in mangrove swamps are more variable. Coastal wetlands provide a variety of ecosystem services to human communities: wetlands can improve water quality, store nutrients, buffer against erosion and storm surge, and provide nursery habitat for commercially and recreationally important fishery species. Current management issues in coastal wetlands include encroaching suburban and agricultural development, sea level rise, nutrient enrichment and eutrophication from agricultural run-off and treated sewage discharge, and freshwater diversion. The policies regulating development on coastal wetlands are complex and dynamic. Restoration is the most common approach to mitigate for anthropogenic impacts. An understanding of wetland ecology is crucial to making wise decisions concerning the nature and direction of restoration projects.
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