Changes
On October 22, 2024, 11:56:28 AM UTC,
-
Added resource mud_fr_metadata.csv to Data from: The effects of gas extraction under intertidal mudflats on sediment and macrozoobenthic communities
| f | 1 | { | f | 1 | { |
| 2 | "author": null, | 2 | "author": null, | ||
| 3 | "author_email": null, | 3 | "author_email": null, | ||
| 4 | "code": "7b.b.ag", | 4 | "code": "7b.b.ag", | ||
| 5 | "contributor": "NIOZ Royal Netherlands Institute for Sea Research", | 5 | "contributor": "NIOZ Royal Netherlands Institute for Sea Research", | ||
| 6 | "creator_user_id": "703d6db1-9abc-4abf-8bc2-5fe6ee77bc2b", | 6 | "creator_user_id": "703d6db1-9abc-4abf-8bc2-5fe6ee77bc2b", | ||
| 7 | "creators": "[{\"firstname\":\"Paula\",\"lastname\":\"de la | 7 | "creators": "[{\"firstname\":\"Paula\",\"lastname\":\"de la | ||
| 8 | cid\":\"https://orcid.org/0000-0001-8416-5926\",\"affiliation\":\"NIOZ | 8 | cid\":\"https://orcid.org/0000-0001-8416-5926\",\"affiliation\":\"NIOZ | ||
| 9 | Royal Netherlands Institute for Sea | 9 | Royal Netherlands Institute for Sea | ||
| 10 | ndingauthor\":false,\"contactemailaddress\":null,\"formatted\":\"Paula | 10 | ndingauthor\":false,\"contactemailaddress\":null,\"formatted\":\"Paula | ||
| 11 | de la Barra - NIOZ Royal Netherlands Institute for Sea Research - | 11 | de la Barra - NIOZ Royal Netherlands Institute for Sea Research - | ||
| 12 | ORCID: https://orcid.org/0000-0001-8416-5926\"},{\"firstname\":\"Geert | 12 | ORCID: https://orcid.org/0000-0001-8416-5926\"},{\"firstname\":\"Geert | ||
| 13 | cid\":\"https://orcid.org/0000-0003-3196-4235\",\"affiliation\":\"NIOZ | 13 | cid\":\"https://orcid.org/0000-0003-3196-4235\",\"affiliation\":\"NIOZ | ||
| 14 | Royal Netherlands Institute for Sea Research, and Wageningen Marine | 14 | Royal Netherlands Institute for Sea Research, and Wageningen Marine | ||
| 15 | Research, Wageningen University and | 15 | Research, Wageningen University and | ||
| 16 | ondingauthor\":null,\"contactemailaddress\":null,\"formatted\":\"Geert | 16 | ondingauthor\":null,\"contactemailaddress\":null,\"formatted\":\"Geert | ||
| 17 | Aarts - NIOZ Royal Netherlands Institute for Sea Research, and | 17 | Aarts - NIOZ Royal Netherlands Institute for Sea Research, and | ||
| 18 | Wageningen Marine Research, Wageningen University and Research - | 18 | Wageningen Marine Research, Wageningen University and Research - | ||
| 19 | ORCID: | 19 | ORCID: | ||
| 20 | cid\":\"https://orcid.org/0000-0002-3159-8944\",\"affiliation\":\"NIOZ | 20 | cid\":\"https://orcid.org/0000-0002-3159-8944\",\"affiliation\":\"NIOZ | ||
| 21 | Royal Netherlands Institute for Sea | 21 | Royal Netherlands Institute for Sea | ||
| 22 | author\":true,\"contactemailaddress\":\"allert.bijleveld@nioz.nl\"}]", | 22 | author\":true,\"contactemailaddress\":\"allert.bijleveld@nioz.nl\"}]", | ||
| 23 | "dataset_persistent_id": "DOI:10.33591/nioz/7b.b.ag", | 23 | "dataset_persistent_id": "DOI:10.33591/nioz/7b.b.ag", | ||
| 24 | "deposit_date": "2023-10-17", | 24 | "deposit_date": "2023-10-17", | ||
| 25 | "depositor": "Allert Bijleveld", | 25 | "depositor": "Allert Bijleveld", | ||
| 26 | "distribution_date": "2023-10-17", | 26 | "distribution_date": "2023-10-17", | ||
| 27 | "distributor": "Research Data Management(NIOZ Royal Netherlands | 27 | "distributor": "Research Data Management(NIOZ Royal Netherlands | ||
| 28 | Institute for Sea Research)", | 28 | Institute for Sea Research)", | ||
| 29 | "doi_date_published": "2023-10-20", | 29 | "doi_date_published": "2023-10-20", | ||
| 30 | "funding_references": "[{\"name\":\"Royal Netherlands Institute for | 30 | "funding_references": "[{\"name\":\"Royal Netherlands Institute for | ||
| 31 | Sea Research | 31 | Sea Research | ||
| 32 | NIOZ)\",\"awardnumber\":null,\"awardtitle\":null,\"formatted\":\"Royal | 32 | NIOZ)\",\"awardnumber\":null,\"awardtitle\":null,\"formatted\":\"Royal | ||
| 33 | Netherlands Institute for Sea Research (NIOZ) - | 33 | Netherlands Institute for Sea Research (NIOZ) - | ||
| 34 | -\"},{\"name\":\"Nederlandse Aardolie Maatschappij | 34 | -\"},{\"name\":\"Nederlandse Aardolie Maatschappij | ||
| 35 | ",\"awardnumber\":null,\"awardtitle\":null,\"formatted\":\"Nederlandse | 35 | ",\"awardnumber\":null,\"awardtitle\":null,\"formatted\":\"Nederlandse | ||
| 36 | Aardolie Maatschappij (NAM) - -\"},{\"name\":\"Rijkswaterstaat | 36 | Aardolie Maatschappij (NAM) - -\"},{\"name\":\"Rijkswaterstaat | ||
| 37 | (RWS)\",\"awardnumber\":null,\"awardtitle\":null}]", | 37 | (RWS)\",\"awardnumber\":null,\"awardtitle\":null}]", | ||
| 38 | "geographic_coverage": "[{\"place\":\"Dutch Wadden | 38 | "geographic_coverage": "[{\"place\":\"Dutch Wadden | ||
| 39 | ude_1\":\"52.88\",\"longitude_2\":\"4.79\",\"latitude_1\":\"7.25\"}]", | 39 | ude_1\":\"52.88\",\"longitude_2\":\"4.79\",\"latitude_1\":\"7.25\"}]", | ||
| 40 | "groups": [], | 40 | "groups": [], | ||
| 41 | "id": "a29fcc6f-c478-409d-b327-c633ef7d057f", | 41 | "id": "a29fcc6f-c478-409d-b327-c633ef7d057f", | ||
| 42 | "isopen": false, | 42 | "isopen": false, | ||
| 43 | "license_title": null, | 43 | "license_title": null, | ||
| 44 | "maintainer": null, | 44 | "maintainer": null, | ||
| 45 | "maintainer_email": null, | 45 | "maintainer_email": null, | ||
| 46 | "metadata_created": "2024-10-22T11:56:26.636866", | 46 | "metadata_created": "2024-10-22T11:56:26.636866", | ||
| n | 47 | "metadata_modified": "2024-10-22T11:56:27.827497", | n | 47 | "metadata_modified": "2024-10-22T11:56:28.410911", |
| 48 | "name": "7bbag", | 48 | "name": "7bbag", | ||
| 49 | "notes": "1-\tLand subsidence in intertidal environments may change | 49 | "notes": "1-\tLand subsidence in intertidal environments may change | ||
| 50 | the flooding regime and sediment composition, two drivers of the | 50 | the flooding regime and sediment composition, two drivers of the | ||
| 51 | macrozoobenthic community. In the Dutch Wadden Sea, a UNESCO world | 51 | macrozoobenthic community. In the Dutch Wadden Sea, a UNESCO world | ||
| 52 | heritage site, gas extraction has resulted in an average subsidence of | 52 | heritage site, gas extraction has resulted in an average subsidence of | ||
| 53 | intertidal mudflats of 2 mm y-1. These mudflats support an abundant | 53 | intertidal mudflats of 2 mm y-1. These mudflats support an abundant | ||
| 54 | macrozoobenthic community that offers important resources for birds | 54 | macrozoobenthic community that offers important resources for birds | ||
| 55 | and fish. The area is managed through the \u201chand on the tap\u201d | 55 | and fish. The area is managed through the \u201chand on the tap\u201d | ||
| 56 | principle, meaning that human activities should be halted if they | 56 | principle, meaning that human activities should be halted if they | ||
| 57 | affect the natural values. To what extent land subsidence affects | 57 | affect the natural values. To what extent land subsidence affects | ||
| 58 | sediment and macrozoobenthos remains unknown and is increasingly | 58 | sediment and macrozoobenthos remains unknown and is increasingly | ||
| 59 | important given sea level rise.\n2-\tTaking advantage of a large-scale | 59 | important given sea level rise.\n2-\tTaking advantage of a large-scale | ||
| 60 | monitoring program, we evaluated the effect of anthropogenically | 60 | monitoring program, we evaluated the effect of anthropogenically | ||
| 61 | caused subsidence on sediment composition and macrozoobenthos. Nearly | 61 | caused subsidence on sediment composition and macrozoobenthos. Nearly | ||
| 62 | 4600 points were sampled yearly (2008-2020) across the Dutch Wadden | 62 | 4600 points were sampled yearly (2008-2020) across the Dutch Wadden | ||
| 63 | Sea, allowing us to compare sediment composition and macrozoobenthos | 63 | Sea, allowing us to compare sediment composition and macrozoobenthos | ||
| 64 | biomass within and outside the subsidence area while controlling for | 64 | biomass within and outside the subsidence area while controlling for | ||
| 65 | the main drivers of these variables. We also compared population | 65 | the main drivers of these variables. We also compared population | ||
| 66 | trends within and outside the subsidence area for 31 species with | 66 | trends within and outside the subsidence area for 31 species with | ||
| 67 | different habitat use.\n3-\tMud fraction was 3% higher within the | 67 | different habitat use.\n3-\tMud fraction was 3% higher within the | ||
| 68 | subsided area and median grain size decreased at 1 \u00b5m y-1 while | 68 | subsided area and median grain size decreased at 1 \u00b5m y-1 while | ||
| 69 | remaining constant in other mudflats. This had no effect on the total | 69 | remaining constant in other mudflats. This had no effect on the total | ||
| 70 | biomass of macrozoobenthos. Within the subsidence area, however, the | 70 | biomass of macrozoobenthos. Within the subsidence area, however, the | ||
| 71 | biomass of species that use deeper areas increased compared to | 71 | biomass of species that use deeper areas increased compared to | ||
| 72 | outside, and the opposite was true for species using shallower | 72 | outside, and the opposite was true for species using shallower | ||
| 73 | habitat.\n4-\tPolicy implications: Land subsidence is related to | 73 | habitat.\n4-\tPolicy implications: Land subsidence is related to | ||
| 74 | changes in median grain size and macrozoobenthic community | 74 | changes in median grain size and macrozoobenthic community | ||
| 75 | composition. However, because thresholds have not been defined, it is | 75 | composition. However, because thresholds have not been defined, it is | ||
| 76 | not clear if this requires management actions. For a successful | 76 | not clear if this requires management actions. For a successful | ||
| 77 | implementation of the \u201chand on the tap\u201d principle in the | 77 | implementation of the \u201chand on the tap\u201d principle in the | ||
| 78 | Wadden Sea, it is necessary to define beforehand the relevant | 78 | Wadden Sea, it is necessary to define beforehand the relevant | ||
| 79 | variables that represent the natural values, implement proper | 79 | variables that represent the natural values, implement proper | ||
| 80 | monitoring, and define thresholds above which effects are not | 80 | monitoring, and define thresholds above which effects are not | ||
| 81 | acceptable. We propose median grain size, mud fraction and | 81 | acceptable. We propose median grain size, mud fraction and | ||
| 82 | macrozoobenthic composition as good measures of the natural values of | 82 | macrozoobenthic composition as good measures of the natural values of | ||
| 83 | the Wadden Sea, and the methods used here as a way for identifying | 83 | the Wadden Sea, and the methods used here as a way for identifying | ||
| 84 | anthropogenic effects on them.", | 84 | anthropogenic effects on them.", | ||
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| 95 | "name": "nioz", | 95 | "name": "nioz", | ||
| 96 | "state": "active", | 96 | "state": "active", | ||
| 97 | "title": "Royal Netherlands Institute for Sea Research", | 97 | "title": "Royal Netherlands Institute for Sea Research", | ||
| 98 | "type": "organization" | 98 | "type": "organization" | ||
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| 149 | } | 171 | } | ||
| 150 | ], | 172 | ], | ||
| 151 | "state": "active", | 173 | "state": "active", | ||
| 152 | "subject": "Earth and Environmental Sciences", | 174 | "subject": "Earth and Environmental Sciences", | ||
| 153 | "tags": [ | 175 | "tags": [ | ||
| 154 | { | 176 | { | ||
| 155 | "display_name": "SIBES", | 177 | "display_name": "SIBES", | ||
| 156 | "id": "dcca6a4c-6f2e-4a5a-bfa8-709d90cbf8f9", | 178 | "id": "dcca6a4c-6f2e-4a5a-bfa8-709d90cbf8f9", | ||
| 157 | "name": "SIBES", | 179 | "name": "SIBES", | ||
| 158 | "state": "active", | 180 | "state": "active", | ||
| 159 | "vocabulary_id": null | 181 | "vocabulary_id": null | ||
| 160 | }, | 182 | }, | ||
| 161 | { | 183 | { | ||
| 162 | "display_name": "Wadden Sea", | 184 | "display_name": "Wadden Sea", | ||
| 163 | "id": "543625c0-3df2-4e6c-95b2-b2a9fda7851e", | 185 | "id": "543625c0-3df2-4e6c-95b2-b2a9fda7851e", | ||
| 164 | "name": "Wadden Sea", | 186 | "name": "Wadden Sea", | ||
| 165 | "state": "active", | 187 | "state": "active", | ||
| 166 | "vocabulary_id": null | 188 | "vocabulary_id": null | ||
| 167 | }, | 189 | }, | ||
| 168 | { | 190 | { | ||
| 169 | "display_name": "anthropogenic impact", | 191 | "display_name": "anthropogenic impact", | ||
| 170 | "id": "fbf8df38-8b9a-4630-9fb2-3989ef23e53d", | 192 | "id": "fbf8df38-8b9a-4630-9fb2-3989ef23e53d", | ||
| 171 | "name": "anthropogenic impact", | 193 | "name": "anthropogenic impact", | ||
| 172 | "state": "active", | 194 | "state": "active", | ||
| 173 | "vocabulary_id": null | 195 | "vocabulary_id": null | ||
| 174 | }, | 196 | }, | ||
| 175 | { | 197 | { | ||
| 176 | "display_name": "benthic invertebrates", | 198 | "display_name": "benthic invertebrates", | ||
| 177 | "id": "690cbef5-deff-4b28-8c91-f7b0d1cbbe20", | 199 | "id": "690cbef5-deff-4b28-8c91-f7b0d1cbbe20", | ||
| 178 | "name": "benthic invertebrates", | 200 | "name": "benthic invertebrates", | ||
| 179 | "state": "active", | 201 | "state": "active", | ||
| 180 | "vocabulary_id": null | 202 | "vocabulary_id": null | ||
| 181 | }, | 203 | }, | ||
| 182 | { | 204 | { | ||
| 183 | "display_name": "inla", | 205 | "display_name": "inla", | ||
| 184 | "id": "62a74de4-b18e-4e39-bb95-46c209e40b9b", | 206 | "id": "62a74de4-b18e-4e39-bb95-46c209e40b9b", | ||
| 185 | "name": "inla", | 207 | "name": "inla", | ||
| 186 | "state": "active", | 208 | "state": "active", | ||
| 187 | "vocabulary_id": null | 209 | "vocabulary_id": null | ||
| 188 | }, | 210 | }, | ||
| 189 | { | 211 | { | ||
| 190 | "display_name": "land subsidence", | 212 | "display_name": "land subsidence", | ||
| 191 | "id": "f2b5736b-b01b-4652-a6bc-76bddabc82e0", | 213 | "id": "f2b5736b-b01b-4652-a6bc-76bddabc82e0", | ||
| 192 | "name": "land subsidence", | 214 | "name": "land subsidence", | ||
| 193 | "state": "active", | 215 | "state": "active", | ||
| 194 | "vocabulary_id": null | 216 | "vocabulary_id": null | ||
| 195 | }, | 217 | }, | ||
| 196 | { | 218 | { | ||
| 197 | "display_name": "macrozoobenthos", | 219 | "display_name": "macrozoobenthos", | ||
| 198 | "id": "0562514f-9682-4fe1-a3ca-56838420e92a", | 220 | "id": "0562514f-9682-4fe1-a3ca-56838420e92a", | ||
| 199 | "name": "macrozoobenthos", | 221 | "name": "macrozoobenthos", | ||
| 200 | "state": "active", | 222 | "state": "active", | ||
| 201 | "vocabulary_id": null | 223 | "vocabulary_id": null | ||
| 202 | }, | 224 | }, | ||
| 203 | { | 225 | { | ||
| 204 | "display_name": "sediment composition", | 226 | "display_name": "sediment composition", | ||
| 205 | "id": "f5e0c2fe-79de-4e91-a35a-5b74e858f56d", | 227 | "id": "f5e0c2fe-79de-4e91-a35a-5b74e858f56d", | ||
| 206 | "name": "sediment composition", | 228 | "name": "sediment composition", | ||
| 207 | "state": "active", | 229 | "state": "active", | ||
| 208 | "vocabulary_id": null | 230 | "vocabulary_id": null | ||
| 209 | }, | 231 | }, | ||
| 210 | { | 232 | { | ||
| 211 | "display_name": "spde", | 233 | "display_name": "spde", | ||
| 212 | "id": "c5751ee3-7037-4e8c-ab6b-7f050db96060", | 234 | "id": "c5751ee3-7037-4e8c-ab6b-7f050db96060", | ||
| 213 | "name": "spde", | 235 | "name": "spde", | ||
| 214 | "state": "active", | 236 | "state": "active", | ||
| 215 | "vocabulary_id": null | 237 | "vocabulary_id": null | ||
| 216 | } | 238 | } | ||
| 217 | ], | 239 | ], | ||
| 218 | "title": "Data from: The effects of gas extraction under intertidal | 240 | "title": "Data from: The effects of gas extraction under intertidal | ||
| 219 | mudflats on sediment and macrozoobenthic communities", | 241 | mudflats on sediment and macrozoobenthic communities", | ||
| 220 | "type": "dataset", | 242 | "type": "dataset", | ||
| 221 | "url": "https://dataportal.nioz.nl/doi/10.33591/nioz/7b.b.ag", | 243 | "url": "https://dataportal.nioz.nl/doi/10.33591/nioz/7b.b.ag", | ||
| 222 | "version": "1" | 244 | "version": "1" | ||
| 223 | } | 245 | } |