6 research outputs found

    Repetitive desiccation events weaken a salt marsh mutualism

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    1. Salt marshes suffered largeā€scale degradation in recent decades. Extreme events such as hot and dry spells contributed significantly to this, and are predicted to increase not only in intensity, but also in frequency under future climate scenarios. Such repetitive extreme events may generate cumulative effects on ecosystem resilience. It is therefore important to elucidate how marsh vegetation responds to repetitive stress, and whether changes in key species interactions can modulate vegetation resilience.2. In this study, we investigated how moderate but repetitive desiccation events, caused by the combined effects of drought and high temperatures, affect cordgrass (<i>Spartina alterniflora</i>), the dominant habitatā€forming grass in southeastern US salt marshes. In a 4ā€month field experiment, we simulated four consecutive desiccation events by periodically excluding tidal flooding and rainfall, while raising temperature. We crossed this desiccation treatment with the presence/absence of ribbed mussels (<i>Geukensia demissa</i>) ā€“ a mutualist of cordgrass known to enhance its desiccation resilience ā€“ and with grazing pressure by the marsh periwinkle (<i>Littoraria irrorate</i>) that is known to suppress cordgrassā€™ desiccation resilience. 3. We found that each subsequent desiccation event deteriorated sediment porewater conditions, resulting in high salinity (53 ppt), low pHā€levels (3.7) and increased porewater Al and Fe concentrations (ā‰ˆ800 Ī¼mol/L and ā‰ˆ1,500 Ī¼mol/L) upon rewetting. No effects on porewater chemistry were found as a result of snail grazing, while ribbed mussels strongly mitigated desiccation effects almost to control levels and increased cordgrass biomass by approximately 128%. Importantly, although cordgrass generally appeared healthy aboveā€ground at the end of the experiment, we found clear negative responses of the repetitive desiccation treatment on cordgrass belowā€ground biomass, on proline (osmolyte) levels in shoots and on the number of tillers (āˆ’40%), regardless of mussel and/or snail presence.4. <i>Synthesis</i>. Even though the mutualism with mussels strongly mitigated chemical effects in the sediment porewater throughout the experiment, mussels could not buffer the adverse ecophysiological effects observed in cordgrass tissue. Our results therefore suggest that although mussels may alleviate desiccation stress, the predicted increased frequency and intensity of hot dry spells may eventually affect saltmarsh resilience by stressing the mutualism beyond its buffering capacity

    Data from: Repetitive desiccation events weaken a salt marsh mutualism

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    Salt marshes suffered largeā€scale degradation in recent decades. Extreme events such as hot and dry spells contributed significantly to this, and are predicted to increase not only in intensity, but also in frequency under future climate scenarios. Such repetitive extreme events may generate cumulative effects on ecosystem resilience. It is therefore important to elucidate how marsh vegetation responds to repetitive stress, and whether changes in key species interactions can modulate vegetation resilience. In this study, we investigated how moderate but repetitive desiccation events, caused by the combined effects of drought and high temperatures, affect cordgrass (Spartina alterniflora), the dominant habitatā€forming grass in southeastern US salt marshes. In a 4ā€month field experiment, we simulated four consecutive desiccation events by periodically excluding tidal flooding and rainfall, while raising temperature. We crossed this desiccation treatment with the presence/absence of ribbed mussels (Geukensia demissa) ā€“ a mutualist of cordgrass known to enhance its desiccation resilience ā€“ and with grazing pressure by the marsh periwinkle (Littoraria irrorata) that is known to suppress cordgrassā€™ desiccation resilience. We found that each subsequent desiccation event deteriorated sediment porewater conditions, resulting in high salinity (53 ppt), low pHā€levels (3.7) and increased porewater Al and Fe concentrations (ā‰ˆ800 Ī¼mol/L and ā‰ˆ1,500 Ī¼mol/L) upon rewetting. No effects on porewater chemistry were found as a result of snail grazing, while ribbed mussels strongly mitigated desiccation effects almost to control levels and increased cordgrass biomass by approximately 128%. Importantly, although cordgrass generally appeared healthy aboveā€ground at the end of the experiment, we found clear negative responses of the repetitive desiccation treatment on cordgrass belowā€ground biomass, on proline (osmolyte) levels in shoots and on the number of tillers (āˆ’40%), regardless of mussel and/or snail presence. Synthesis. Even though the mutualism with mussels strongly mitigated chemical effects in the sediment porewater throughout the experiment, mussels could not buffer the adverse ecophysiological effects observed in cordgrass tissue. Our results therefore suggest that although mussels may alleviate desiccation stress, the predicted increased frequency and intensity of hot dry spells may eventually affect saltmarsh resilience by stressing the mutualism beyond its buffering capacity

    Dataset-Repetitive desiccation events weaken a salt marsh mutualism

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    This dataset contains the data from a field experiment that was conducted from April 2014 till August 2014. We crossed the presence of mussels and snails with a desiccation treatment to test the hypotheses that: 1) multiple chemical stressors accumulate after each successive desiccation event, 2) mussels facilitate cordgrass by mitigating chemical stressors, and 3) snails reduce cordgrassā€™ resilience to withstand these stressors over time. The first data sheet shows data on cordgrass growth, mussels, chemical porewater and plant characteristics averaged per experimental plot. The second data sheet displays chemical porewater concentrations in four consecutive months. The third data sheet shows data about temperature en relative humidity

    Burrowing crabs weaken mutualism between foundation species

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    Dataset for manuscript: Burrowing crabs weaken mutualism between foundation species - Ecosystems 2018. The dataset contains the data on the experiment and field survey carried out in 2014 and 2015. The experiment lasted 16 months and was designed to test how the overlapping presence of two foundation species (cordgrass -Spartina alterniflora, and ribbed mussels -Geukensia demissa) in a southeastern US saltmarsh influenced the abundance of a facilitated species (fiddler crabs - Uca pugnax), and how this species affected each foundation species and their mutualistic interaction. In addition a field survey was conducted spanning 700 km of southeastern US coastline to assess the generality of the interactions found in the experiment. The full methodology can be found in the paper, linked below

    Data from: Repetitive desiccation events weaken a salt marsh mutualism

    No full text
    Salt marshes suffered largeā€scale degradation in recent decades. Extreme events such as hot and dry spells contributed significantly to this, and are predicted to increase not only in intensity, but also in frequency under future climate scenarios. Such repetitive extreme events may generate cumulative effects on ecosystem resilience. It is therefore important to elucidate how marsh vegetation responds to repetitive stress, and whether changes in key species interactions can modulate vegetation resilience. In this study, we investigated how moderate but repetitive desiccation events, caused by the combined effects of drought and high temperatures, affect cordgrass (Spartina alterniflora), the dominant habitatā€forming grass in southeastern US salt marshes. In a 4ā€month field experiment, we simulated four consecutive desiccation events by periodically excluding tidal flooding and rainfall, while raising temperature. We crossed this desiccation treatment with the presence/absence of ribbed mussels (Geukensia demissa) ā€“ a mutualist of cordgrass known to enhance its desiccation resilience ā€“ and with grazing pressure by the marsh periwinkle (Littoraria irrorata) that is known to suppress cordgrassā€™ desiccation resilience. We found that each subsequent desiccation event deteriorated sediment porewater conditions, resulting in high salinity (53 ppt), low pHā€levels (3.7) and increased porewater Al and Fe concentrations (ā‰ˆ800 Ī¼mol/L and ā‰ˆ1,500 Ī¼mol/L) upon rewetting. No effects on porewater chemistry were found as a result of snail grazing, while ribbed mussels strongly mitigated desiccation effects almost to control levels and increased cordgrass biomass by approximately 128%. Importantly, although cordgrass generally appeared healthy aboveā€ground at the end of the experiment, we found clear negative responses of the repetitive desiccation treatment on cordgrass belowā€ground biomass, on proline (osmolyte) levels in shoots and on the number of tillers (āˆ’40%), regardless of mussel and/or snail presence. Synthesis. Even though the mutualism with mussels strongly mitigated chemical effects in the sediment porewater throughout the experiment, mussels could not buffer the adverse ecophysiological effects observed in cordgrass tissue. Our results therefore suggest that although mussels may alleviate desiccation stress, the predicted increased frequency and intensity of hot dry spells may eventually affect saltmarsh resilience by stressing the mutualism beyond its buffering capacity.,Dataset-Repetitive desiccation events weaken a salt marsh mutualismThis dataset contains the data from a field experiment that was conducted from April 2014 till August 2014. We crossed the presence of mussels and snails with a desiccation treatment to test the hypotheses that: 1) multiple chemical stressors accumulate after each successive desiccation event, 2) mussels facilitate cordgrass by mitigating chemical stressors, and 3) snails reduce cordgrassā€™ resilience to withstand these stressors over time. The first data sheet shows data on cordgrass growth, mussels, chemical porewater and plant characteristics averaged per experimental plot. The second data sheet displays chemical porewater concentrations in four consecutive months. The third data sheet shows data about temperature en relative humidity.
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