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On October 22, 2024, 11:50:59 AM UTC,
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Added resource readme_VanDeVen_FE2023.rtf to Data from: Establishing cordgrass plants cluster their shoots to avoid ecosystem engineering
| f | 1 | { | f | 1 | { |
| 2 | "author": null, | 2 | "author": null, | ||
| 3 | "author_email": null, | 3 | "author_email": null, | ||
| 4 | "code": "7b.b.2d", | 4 | "code": "7b.b.2d", | ||
| 5 | "contributor": "NIOZ Royal Netherlands Institute for Sea Research", | 5 | "contributor": "NIOZ Royal Netherlands Institute for Sea Research", | ||
| 6 | "creator_user_id": "32b8c7bf-e762-4c04-8457-7610343a5404", | 6 | "creator_user_id": "32b8c7bf-e762-4c04-8457-7610343a5404", | ||
| 7 | "creators": "[{\"firstname\":\"Clea\",\"lastname\":\"van de | 7 | "creators": "[{\"firstname\":\"Clea\",\"lastname\":\"van de | ||
| 8 | id\":\"https://orcid.org/0000-0002-9127-9929\",\"affiliation\":\"Royal | 8 | id\":\"https://orcid.org/0000-0002-9127-9929\",\"affiliation\":\"Royal | ||
| 9 | Netherlands Institute for Sea | 9 | Netherlands Institute for Sea | ||
| 10 | gauthor\":true,\"contactemailaddress\":\"clea.van.de.ven@nioz.nl\"}]", | 10 | gauthor\":true,\"contactemailaddress\":\"clea.van.de.ven@nioz.nl\"}]", | ||
| 11 | "dataset_persistent_id": "DOI:10.33591/nioz/7b.b.2d", | 11 | "dataset_persistent_id": "DOI:10.33591/nioz/7b.b.2d", | ||
| 12 | "deposit_date": "2023-02-01", | 12 | "deposit_date": "2023-02-01", | ||
| 13 | "depositor": "Clea Ven van de", | 13 | "depositor": "Clea Ven van de", | ||
| 14 | "distribution_date": "2023-02-01", | 14 | "distribution_date": "2023-02-01", | ||
| 15 | "distributor": "Research Data Management(NIOZ Royal Netherlands | 15 | "distributor": "Research Data Management(NIOZ Royal Netherlands | ||
| 16 | Institute for Sea Research)", | 16 | Institute for Sea Research)", | ||
| 17 | "doi_date_published": "2023-02-03", | 17 | "doi_date_published": "2023-02-03", | ||
| 18 | "funding_references": "", | 18 | "funding_references": "", | ||
| 19 | "geographic_coverage": "[{\"place\":\"NW | 19 | "geographic_coverage": "[{\"place\":\"NW | ||
| 20 | null,\"longitude_1\":null,\"longitude_2\":null,\"latitude_1\":null}]", | 20 | null,\"longitude_1\":null,\"longitude_2\":null,\"latitude_1\":null}]", | ||
| 21 | "groups": [], | 21 | "groups": [], | ||
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| 24 | "license_title": null, | 24 | "license_title": null, | ||
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| 27 | "metadata_created": "2024-10-22T11:50:58.551470", | 27 | "metadata_created": "2024-10-22T11:50:58.551470", | ||
| n | 28 | "metadata_modified": "2024-10-22T11:50:59.106706", | n | 28 | "metadata_modified": "2024-10-22T11:50:59.413124", |
| 29 | "name": "7bb2d", | 29 | "name": "7bb2d", | ||
| 30 | "notes": "1.\tVegetated coastal ecosystems such as salt marshes, | 30 | "notes": "1.\tVegetated coastal ecosystems such as salt marshes, | ||
| 31 | dunes and seagrass meadows occur at the land-sea interface \u2013 a | 31 | dunes and seagrass meadows occur at the land-sea interface \u2013 a | ||
| 32 | dynamic environment typified by harsh growing conditions. These | 32 | dynamic environment typified by harsh growing conditions. These | ||
| 33 | ecosystems are known as biogeomorphic landscapes because their | 33 | ecosystems are known as biogeomorphic landscapes because their | ||
| 34 | functioning depends on biophysical interactions by which organisms | 34 | functioning depends on biophysical interactions by which organisms | ||
| 35 | engineer landforms to their own benefit. The strength of such | 35 | engineer landforms to their own benefit. The strength of such | ||
| 36 | biogeomorphic feedbacks depends on plant traits, such as stem | 36 | biogeomorphic feedbacks depends on plant traits, such as stem | ||
| 37 | flexibility and shoot density. \n2.\tRecent work demonstrated that | 37 | flexibility and shoot density. \n2.\tRecent work demonstrated that | ||
| 38 | dune grasses with similar morphological traits can build contrasting | 38 | dune grasses with similar morphological traits can build contrasting | ||
| 39 | landscapes due to differences in their spatial shoot organization. | 39 | landscapes due to differences in their spatial shoot organization. | ||
| 40 | However, in contrast to dune grasses that trap and stabilize sand | 40 | However, in contrast to dune grasses that trap and stabilize sand | ||
| 41 | particles in aeolian landscapes, flow attenuation in aquatic | 41 | particles in aeolian landscapes, flow attenuation in aquatic | ||
| 42 | environments can generate scouring around plant stems and cause | 42 | environments can generate scouring around plant stems and cause | ||
| 43 | uprooting, leading to establishment thresholds for young | 43 | uprooting, leading to establishment thresholds for young | ||
| 44 | plants.\n3.\tYet, it remains unknown how findings from aeolian | 44 | plants.\n3.\tYet, it remains unknown how findings from aeolian | ||
| 45 | landscapes translate to aquatic systems and how young clonally | 45 | landscapes translate to aquatic systems and how young clonally | ||
| 46 | expanding plants in hydrodynamically exposed conditions overcome these | 46 | expanding plants in hydrodynamically exposed conditions overcome these | ||
| 47 | establishment thresholds by optimizing shoot placement. \n4.\tHere, we | 47 | establishment thresholds by optimizing shoot placement. \n4.\tHere, we | ||
| 48 | measured shoot patterns of 90 establishing cordgrass patches (Spartina | 48 | measured shoot patterns of 90 establishing cordgrass patches (Spartina | ||
| 49 | anglica) at 18 European field sites that cover a broad range of | 49 | anglica) at 18 European field sites that cover a broad range of | ||
| 50 | hydrodynamic conditions. Next, we carried out a field experiment to | 50 | hydrodynamic conditions. Next, we carried out a field experiment to | ||
| 51 | investigate how observed spatial shoot patterns affect plant-sediment | 51 | investigate how observed spatial shoot patterns affect plant-sediment | ||
| 52 | feedbacks. \n5.\tSurprisingly, field survey analyses reveal highly | 52 | feedbacks. \n5.\tSurprisingly, field survey analyses reveal highly | ||
| 53 | consistent clustered shoot patterns, regardless of environmental | 53 | consistent clustered shoot patterns, regardless of environmental | ||
| 54 | conditions. Experimental results demonstrate that this clustered | 54 | conditions. Experimental results demonstrate that this clustered | ||
| 55 | pattern minimizes scouring compared to densely clumped organizations | 55 | pattern minimizes scouring compared to densely clumped organizations | ||
| 56 | typically observed in established patches.\n6.\tSynthesis. In contrast | 56 | typically observed in established patches.\n6.\tSynthesis. In contrast | ||
| 57 | to earlier findings highlighting that establishing dune grasses | 57 | to earlier findings highlighting that establishing dune grasses | ||
| 58 | optimize their landscape engineering capacity via a flexible shoot | 58 | optimize their landscape engineering capacity via a flexible shoot | ||
| 59 | placement strategy, we find that cordgrass instead follows a fixed | 59 | placement strategy, we find that cordgrass instead follows a fixed | ||
| 60 | strategy that minimizes engineering effects in its early life stages. | 60 | strategy that minimizes engineering effects in its early life stages. | ||
| 61 | We suggest that marsh grasses avoid physical stress and associated | 61 | We suggest that marsh grasses avoid physical stress and associated | ||
| 62 | establishment thresholds in their early life stage, and switch to an | 62 | establishment thresholds in their early life stage, and switch to an | ||
| 63 | ecosystem engineering strategy once established. These findings shed | 63 | ecosystem engineering strategy once established. These findings shed | ||
| 64 | new light on how plant traits interact with their environment to shape | 64 | new light on how plant traits interact with their environment to shape | ||
| 65 | the landscape and pave the way for improved restoration designs by | 65 | the landscape and pave the way for improved restoration designs by | ||
| 66 | mimicking the natural shoot organization of establishing vegetation.", | 66 | mimicking the natural shoot organization of establishing vegetation.", | ||
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| 135 | "tags": [ | 157 | "tags": [ | ||
| 136 | { | 158 | { | ||
| 137 | "display_name": "Vegetated coastal ecosystems Salt marshes | 159 | "display_name": "Vegetated coastal ecosystems Salt marshes | ||
| 138 | Clonal expansion strategy Shoot organisation Establishm", | 160 | Clonal expansion strategy Shoot organisation Establishm", | ||
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| 140 | "name": "Vegetated coastal ecosystems Salt marshes Clonal | 162 | "name": "Vegetated coastal ecosystems Salt marshes Clonal | ||
| 141 | expansion strategy Shoot organisation Establishm", | 163 | expansion strategy Shoot organisation Establishm", | ||
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| 146 | "title": "Data from: Establishing cordgrass plants cluster their | 168 | "title": "Data from: Establishing cordgrass plants cluster their | ||
| 147 | shoots to avoid ecosystem engineering", | 169 | shoots to avoid ecosystem engineering", | ||
| 148 | "type": "dataset", | 170 | "type": "dataset", | ||
| 149 | "url": "https://dataportal.nioz.nl/doi/10.33591/nioz/7b.b.2d", | 171 | "url": "https://dataportal.nioz.nl/doi/10.33591/nioz/7b.b.2d", | ||
| 150 | "version": "1" | 172 | "version": "1" | ||
| 151 | } | 173 | } |