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On October 22, 2024, 6:01:02 PM UTC,
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Added resource PublicData_zeeland 2020.xlsx to Co-occurring intertidal ecosystem engineers with opposing growth strategies show opposite responses to environmental gradients during establishment
| f | 1 | { | f | 1 | { |
| 2 | "author": null, | 2 | "author": null, | ||
| 3 | "author_email": null, | 3 | "author_email": null, | ||
| 4 | "code": "7b.b.9g", | 4 | "code": "7b.b.9g", | ||
| 5 | "contributor": "NIOZ Royal Netherlands Institute for Sea Research", | 5 | "contributor": "NIOZ Royal Netherlands Institute for Sea Research", | ||
| 6 | "creator_user_id": "deb45017-069c-4010-aedf-8de5062465c6", | 6 | "creator_user_id": "deb45017-069c-4010-aedf-8de5062465c6", | ||
| 7 | "creators": "[{\"firstname\":\"Clea\",\"lastname\":\"van de | 7 | "creators": "[{\"firstname\":\"Clea\",\"lastname\":\"van de | ||
| 8 | Ven\",\"orcid\":null,\"affiliation\":\"Royal Netherlands Institute for | 8 | Ven\",\"orcid\":null,\"affiliation\":\"Royal Netherlands Institute for | ||
| 9 | Sea | 9 | Sea | ||
| 10 | contactemailaddress\":\"clea.van.de.ven@nioz.nl\",\"formatted\":\"Clea | 10 | contactemailaddress\":\"clea.van.de.ven@nioz.nl\",\"formatted\":\"Clea | ||
| 11 | van de Ven - Royal Netherlands Institute for Sea Research - ORCID: - | 11 | van de Ven - Royal Netherlands Institute for Sea Research - ORCID: - | ||
| 12 | Corresponding Author - clea.van.de.ven@nioz.nl\"}]", | 12 | Corresponding Author - clea.van.de.ven@nioz.nl\"}]", | ||
| 13 | "dataset_persistent_id": "DOI:10.25850/nioz/7b.b.9g", | 13 | "dataset_persistent_id": "DOI:10.25850/nioz/7b.b.9g", | ||
| 14 | "deposit_date": "2024-03-15", | 14 | "deposit_date": "2024-03-15", | ||
| 15 | "depositor": "Clea Ven van de", | 15 | "depositor": "Clea Ven van de", | ||
| 16 | "distribution_date": "2024-03-15", | 16 | "distribution_date": "2024-03-15", | ||
| 17 | "distributor": "Research Data Management(NIOZ Royal Netherlands | 17 | "distributor": "Research Data Management(NIOZ Royal Netherlands | ||
| 18 | Institute for Sea Research)", | 18 | Institute for Sea Research)", | ||
| 19 | "doi_date_published": "2024-03-15", | 19 | "doi_date_published": "2024-03-15", | ||
| 20 | "funding_references": "[{\"name\":\"NWO\",\"awardnumber\":\"VIDI | 20 | "funding_references": "[{\"name\":\"NWO\",\"awardnumber\":\"VIDI | ||
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| 22 | - VIDI | 22 | - VIDI | ||
| 23 | ":\"Veni.212.059\",\"awardtitle\":\"Veni.212.059\",\"formatted\":\"NWO | 23 | ":\"Veni.212.059\",\"awardtitle\":\"Veni.212.059\",\"formatted\":\"NWO | ||
| 24 | - Veni.212.059 - Veni.212.059\"}]", | 24 | - Veni.212.059 - Veni.212.059\"}]", | ||
| 25 | "geographic_coverage": "[{\"place\":\"Zeeland, | 25 | "geographic_coverage": "[{\"place\":\"Zeeland, | ||
| 26 | de_2\":\"3.81937\",\"latitude_1\":\"4.11985\",\"formatted\":\"Zeeland, | 26 | de_2\":\"3.81937\",\"latitude_1\":\"4.11985\",\"formatted\":\"Zeeland, | ||
| 27 | Netherlands N: 51.67517 S: 51.38587 E: 4.11985 W: 3.81937\"}]", | 27 | Netherlands N: 51.67517 S: 51.38587 E: 4.11985 W: 3.81937\"}]", | ||
| 28 | "groups": [], | 28 | "groups": [], | ||
| 29 | "id": "7f60d24e-66dd-4449-b5e6-091f3f1b587e", | 29 | "id": "7f60d24e-66dd-4449-b5e6-091f3f1b587e", | ||
| 30 | "isopen": false, | 30 | "isopen": false, | ||
| 31 | "license_title": null, | 31 | "license_title": null, | ||
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| 34 | "metadata_created": "2024-10-22T18:01:01.425138", | 34 | "metadata_created": "2024-10-22T18:01:01.425138", | ||
| n | 35 | "metadata_modified": "2024-10-22T18:01:01.425145", | n | 35 | "metadata_modified": "2024-10-22T18:01:02.664162", |
| 36 | "name": "7bb9g", | 36 | "name": "7bb9g", | ||
| 37 | "notes": "Coastal vegetated ecosystems including mangroves, | 37 | "notes": "Coastal vegetated ecosystems including mangroves, | ||
| 38 | seagrasses, and salt marshes are often shaped by positive | 38 | seagrasses, and salt marshes are often shaped by positive | ||
| 39 | plant-environment feedbacks. Plants improve their own living | 39 | plant-environment feedbacks. Plants improve their own living | ||
| 40 | conditions with increasing patch size and density by attenuating | 40 | conditions with increasing patch size and density by attenuating | ||
| 41 | hydrodynamics and stabilizing sediments. As these habitat | 41 | hydrodynamics and stabilizing sediments. As these habitat | ||
| 42 | modifications are critical for survival and growth, the positive | 42 | modifications are critical for survival and growth, the positive | ||
| 43 | density-dependent nature of these feedbacks can lead to establishment | 43 | density-dependent nature of these feedbacks can lead to establishment | ||
| 44 | thresholds for young plants in absence of mature conspecifics. | 44 | thresholds for young plants in absence of mature conspecifics. | ||
| 45 | Although feedback strength is known to depend on hydrodynamic exposure | 45 | Although feedback strength is known to depend on hydrodynamic exposure | ||
| 46 | and plant traits (e.g. stiff vs flexible stems), it remains unclear | 46 | and plant traits (e.g. stiff vs flexible stems), it remains unclear | ||
| 47 | how (1) opposing morphological plant traits affect establishment in | 47 | how (1) opposing morphological plant traits affect establishment in | ||
| 48 | contrasting environments, and (2) whether trait plasticity influences | 48 | contrasting environments, and (2) whether trait plasticity influences | ||
| 49 | establishment success. Here, we investigate this by transplanting two | 49 | establishment success. Here, we investigate this by transplanting two | ||
| 50 | tidal species with opposing growing strategies \u2013 Spartina | 50 | tidal species with opposing growing strategies \u2013 Spartina | ||
| 51 | anglica forms tussocks of stiff stems while Zostera noltii forms | 51 | anglica forms tussocks of stiff stems while Zostera noltii forms | ||
| 52 | patches of stress-avoiding flexible shoots \u2013 from two different | 52 | patches of stress-avoiding flexible shoots \u2013 from two different | ||
| 53 | donor sites in 8 experimental locations. \n\tResults show that the | 53 | donor sites in 8 experimental locations. \n\tResults show that the | ||
| 54 | survival and growth of both species was most successful at field | 54 | survival and growth of both species was most successful at field | ||
| 55 | locations with diverging environmental characteristics, while overall | 55 | locations with diverging environmental characteristics, while overall | ||
| 56 | survival was highest for Z. noltii. Mainly, S. anglica survival was | 56 | survival was highest for Z. noltii. Mainly, S. anglica survival was | ||
| 57 | highest at locations with high organic matter and silt content and | 57 | highest at locations with high organic matter and silt content and | ||
| 58 | higher elevation relative to the tidal amplitude. In contrast, Z. | 58 | higher elevation relative to the tidal amplitude. In contrast, Z. | ||
| 59 | noltii survival was highest at locations with larger grainsize and | 59 | noltii survival was highest at locations with larger grainsize and | ||
| 60 | lower relative elevations. Furthermore, despite initial differences in | 60 | lower relative elevations. Furthermore, despite initial differences in | ||
| 61 | plant traits between the two donor sites of Z. noltii, we found no | 61 | plant traits between the two donor sites of Z. noltii, we found no | ||
| 62 | effects of donor origin. Contrastingly, we found a significant effect | 62 | effects of donor origin. Contrastingly, we found a significant effect | ||
| 63 | of donor origin on S. anglica growth, even though transplants from the | 63 | of donor origin on S. anglica growth, even though transplants from the | ||
| 64 | two donor sites showed no initial trait differences. Collectively, | 64 | two donor sites showed no initial trait differences. Collectively, | ||
| 65 | these results suggest that the stress-tolerance strategy of S. anglica | 65 | these results suggest that the stress-tolerance strategy of S. anglica | ||
| 66 | hampers establishment in exposed conditions, whereas the | 66 | hampers establishment in exposed conditions, whereas the | ||
| 67 | stress-avoiding Z. noltii appears to be more susceptible to stress | 67 | stress-avoiding Z. noltii appears to be more susceptible to stress | ||
| 68 | from desiccation and silty sediments.", | 68 | from desiccation and silty sediments.", | ||
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| 72 | "approval_status": "approved", | 72 | "approval_status": "approved", | ||
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| 80 | "state": "active", | 80 | "state": "active", | ||
| 81 | "title": "Royal Netherlands Institute for Sea Research", | 81 | "title": "Royal Netherlands Institute for Sea Research", | ||
| 82 | "type": "organization" | 82 | "type": "organization" | ||
| 83 | }, | 83 | }, | ||
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| 86 | "production_date": "2024-03-15", | 86 | "production_date": "2024-03-15", | ||
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| 90 | "state": "active", | 114 | "state": "active", | ||
| 91 | "subject": "Earth and Environmental Sciences", | 115 | "subject": "Earth and Environmental Sciences", | ||
| 92 | "tags": [ | 116 | "tags": [ | ||
| 93 | { | 117 | { | ||
| 94 | "display_name": "Spartina anglica", | 118 | "display_name": "Spartina anglica", | ||
| 95 | "id": "506ba9dc-34cf-4580-848b-45130c2e74d0", | 119 | "id": "506ba9dc-34cf-4580-848b-45130c2e74d0", | ||
| 96 | "name": "Spartina anglica", | 120 | "name": "Spartina anglica", | ||
| 97 | "state": "active", | 121 | "state": "active", | ||
| 98 | "vocabulary_id": null | 122 | "vocabulary_id": null | ||
| 99 | }, | 123 | }, | ||
| 100 | { | 124 | { | ||
| 101 | "display_name": "Zostera noltii", | 125 | "display_name": "Zostera noltii", | ||
| 102 | "id": "f6755bed-21c3-4fb5-bdb0-f4c82764eb09", | 126 | "id": "f6755bed-21c3-4fb5-bdb0-f4c82764eb09", | ||
| 103 | "name": "Zostera noltii", | 127 | "name": "Zostera noltii", | ||
| 104 | "state": "active", | 128 | "state": "active", | ||
| 105 | "vocabulary_id": null | 129 | "vocabulary_id": null | ||
| 106 | }, | 130 | }, | ||
| 107 | { | 131 | { | ||
| 108 | "display_name": "ecosystem engineers", | 132 | "display_name": "ecosystem engineers", | ||
| 109 | "id": "a241c607-4d89-4f10-8e7d-5ebeb1d62f3f", | 133 | "id": "a241c607-4d89-4f10-8e7d-5ebeb1d62f3f", | ||
| 110 | "name": "ecosystem engineers", | 134 | "name": "ecosystem engineers", | ||
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| 112 | "vocabulary_id": null | 136 | "vocabulary_id": null | ||
| 113 | }, | 137 | }, | ||
| 114 | { | 138 | { | ||
| 115 | "display_name": "establishment", | 139 | "display_name": "establishment", | ||
| 116 | "id": "605cafc2-c5d2-4d80-a38d-1b40607bedcd", | 140 | "id": "605cafc2-c5d2-4d80-a38d-1b40607bedcd", | ||
| 117 | "name": "establishment", | 141 | "name": "establishment", | ||
| 118 | "state": "active", | 142 | "state": "active", | ||
| 119 | "vocabulary_id": null | 143 | "vocabulary_id": null | ||
| 120 | }, | 144 | }, | ||
| 121 | { | 145 | { | ||
| 122 | "display_name": "intertidal wetlands", | 146 | "display_name": "intertidal wetlands", | ||
| 123 | "id": "075eab60-8acf-4819-a1db-8d750057dad6", | 147 | "id": "075eab60-8acf-4819-a1db-8d750057dad6", | ||
| 124 | "name": "intertidal wetlands", | 148 | "name": "intertidal wetlands", | ||
| 125 | "state": "active", | 149 | "state": "active", | ||
| 126 | "vocabulary_id": null | 150 | "vocabulary_id": null | ||
| 127 | }, | 151 | }, | ||
| 128 | { | 152 | { | ||
| 129 | "display_name": "stress avoidance", | 153 | "display_name": "stress avoidance", | ||
| 130 | "id": "d5bc1dee-f0ad-4e8a-987a-737fc518fc91", | 154 | "id": "d5bc1dee-f0ad-4e8a-987a-737fc518fc91", | ||
| 131 | "name": "stress avoidance", | 155 | "name": "stress avoidance", | ||
| 132 | "state": "active", | 156 | "state": "active", | ||
| 133 | "vocabulary_id": null | 157 | "vocabulary_id": null | ||
| 134 | }, | 158 | }, | ||
| 135 | { | 159 | { | ||
| 136 | "display_name": "stress tolerance", | 160 | "display_name": "stress tolerance", | ||
| 137 | "id": "c06a395b-76db-4087-b5ec-9df1704f1e18", | 161 | "id": "c06a395b-76db-4087-b5ec-9df1704f1e18", | ||
| 138 | "name": "stress tolerance", | 162 | "name": "stress tolerance", | ||
| 139 | "state": "active", | 163 | "state": "active", | ||
| 140 | "vocabulary_id": null | 164 | "vocabulary_id": null | ||
| 141 | } | 165 | } | ||
| 142 | ], | 166 | ], | ||
| 143 | "title": "Co-occurring intertidal ecosystem engineers with opposing | 167 | "title": "Co-occurring intertidal ecosystem engineers with opposing | ||
| 144 | growth strategies show opposite responses to environmental gradients | 168 | growth strategies show opposite responses to environmental gradients | ||
| 145 | during establishment", | 169 | during establishment", | ||
| 146 | "type": "dataset", | 170 | "type": "dataset", | ||
| 147 | "url": "https://dataportal.nioz.nl/doi/10.25850/nioz/7b.b.9g", | 171 | "url": "https://dataportal.nioz.nl/doi/10.25850/nioz/7b.b.9g", | ||
| 148 | "version": "1" | 172 | "version": "1" | ||
| 149 | } | 173 | } |