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Subido un nuevo fichero al recurso README.txt en Assessing impacts of social-ecological diversity on resilience in a wetland coupled human and natural system: Data release
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ahttps://digital.csic.es/bitstream/10261/280602/7/README.txt
en recurso README.txt en Assessing impacts of social-ecological diversity on resilience in a wetland coupled human and natural system: Data release
| f | 1 | { | f | 1 | { |
| 2 | "Observaciones": { | 2 | "Observaciones": { | ||
| 3 | "en": "Recommended citation: Van Schmidt, Nathan D.; Oviedo, | 3 | "en": "Recommended citation: Van Schmidt, Nathan D.; Oviedo, | ||
| 4 | Jos\u00e9 L.; Hruska, Tracy; Huntsinger, Lynn; Kovach, Tony; | 4 | Jos\u00e9 L.; Hruska, Tracy; Huntsinger, Lynn; Kovach, Tony; | ||
| 5 | Kilpatrick, A. Marm; Miller, Norman L.; Beissinger, Steven R.; 2021; | 5 | Kilpatrick, A. Marm; Miller, Norman L.; Beissinger, Steven R.; 2021; | ||
| 6 | Assessing impacts of social-ecological diversity on resilience in a | 6 | Assessing impacts of social-ecological diversity on resilience in a | ||
| 7 | wetland coupled human and natural system: Data release [Dataset]; | 7 | wetland coupled human and natural system: Data release [Dataset]; | ||
| 8 | Dryad; Version 4; https://doi.org/10.6078/D1970G", | 8 | Dryad; Version 4; https://doi.org/10.6078/D1970G", | ||
| 9 | "es": "Cita recomendada: Van Schmidt, Nathan D.; Oviedo, Jos\u00e9 | 9 | "es": "Cita recomendada: Van Schmidt, Nathan D.; Oviedo, Jos\u00e9 | ||
| 10 | L.; Hruska, Tracy; Huntsinger, Lynn; Kovach, Tony; Kilpatrick, A. | 10 | L.; Hruska, Tracy; Huntsinger, Lynn; Kovach, Tony; Kilpatrick, A. | ||
| 11 | Marm; Miller, Norman L.; Beissinger, Steven R.; 2021; Assessing | 11 | Marm; Miller, Norman L.; Beissinger, Steven R.; 2021; Assessing | ||
| 12 | impacts of social-ecological diversity on resilience in a wetland | 12 | impacts of social-ecological diversity on resilience in a wetland | ||
| 13 | coupled human and natural system: Data release [Dataset]; Dryad; | 13 | coupled human and natural system: Data release [Dataset]; Dryad; | ||
| 14 | Version 4; https://doi.org/10.6078/D1970G" | 14 | Version 4; https://doi.org/10.6078/D1970G" | ||
| 15 | }, | 15 | }, | ||
| 16 | "author": null, | 16 | "author": null, | ||
| 17 | "author_email": null, | 17 | "author_email": null, | ||
| 18 | "autor": { | 18 | "autor": { | ||
| 19 | "en": [ | 19 | "en": [ | ||
| 20 | "Nathan D. Van Schmidt", | 20 | "Nathan D. Van Schmidt", | ||
| 21 | "Jos\u00e9 L. Oviedo", | 21 | "Jos\u00e9 L. Oviedo", | ||
| 22 | "Tracy Hruska", | 22 | "Tracy Hruska", | ||
| 23 | "Lynn Huntsinger", | 23 | "Lynn Huntsinger", | ||
| 24 | "Tony Kovach", | 24 | "Tony Kovach", | ||
| 25 | "A. Marm Kilpatrick", | 25 | "A. Marm Kilpatrick", | ||
| 26 | "Norman L. Miller", | 26 | "Norman L. Miller", | ||
| 27 | "Steven R. Beissinger" | 27 | "Steven R. Beissinger" | ||
| 28 | ], | 28 | ], | ||
| 29 | "es": [ | 29 | "es": [ | ||
| 30 | "Nathan D. Van Schmidt", | 30 | "Nathan D. Van Schmidt", | ||
| 31 | "Jos\u00e9 L. Oviedo", | 31 | "Jos\u00e9 L. Oviedo", | ||
| 32 | "Tracy Hruska", | 32 | "Tracy Hruska", | ||
| 33 | "Lynn Huntsinger", | 33 | "Lynn Huntsinger", | ||
| 34 | "Tony Kovach", | 34 | "Tony Kovach", | ||
| 35 | "A. Marm Kilpatrick", | 35 | "A. Marm Kilpatrick", | ||
| 36 | "Norman L. Miller", | 36 | "Norman L. Miller", | ||
| 37 | "Steven R. Beissinger" | 37 | "Steven R. Beissinger" | ||
| 38 | ] | 38 | ] | ||
| 39 | }, | 39 | }, | ||
| 40 | "conforms_to": [], | 40 | "conforms_to": [], | ||
| 41 | "coverage_new": {}, | 41 | "coverage_new": {}, | ||
| 42 | "creator_user_id": "196556b3-e0c4-4c51-a9e6-f51cc752bc37", | 42 | "creator_user_id": "196556b3-e0c4-4c51-a9e6-f51cc752bc37", | ||
| 43 | "description": { | 43 | "description": { | ||
| 44 | "en": "[Methods] We mapped all emergent wetlands > 5\u00d75 m | 44 | "en": "[Methods] We mapped all emergent wetlands > 5\u00d75 m | ||
| 45 | within our study area\u2014California\u2019s Sierra Nevada foothills | 45 | within our study area\u2014California\u2019s Sierra Nevada foothills | ||
| 46 | EPA zone III eco-region in Yuba, Nevada, and southern Butte countieso | 46 | EPA zone III eco-region in Yuba, Nevada, and southern Butte countieso | ||
| 47 | of California. Mapping was done by manually interpreting summer 2013 | 47 | of California. Mapping was done by manually interpreting summer 2013 | ||
| 48 | GeoEye-1 0.4 m imagery in Google Earth 7.1.5. Areas covered by | 48 | GeoEye-1 0.4 m imagery in Google Earth 7.1.5. Areas covered by | ||
| 49 | hydrophytes (Typha spp., Scirpus spp., Juncus effusus, Leersia | 49 | hydrophytes (Typha spp., Scirpus spp., Juncus effusus, Leersia | ||
| 50 | oryzoides, or various sedges) were considered wetland. We included | 50 | oryzoides, or various sedges) were considered wetland. We included | ||
| 51 | hydrophytes that appeared seasonally dried; if green vegetation was | 51 | hydrophytes that appeared seasonally dried; if green vegetation was | ||
| 52 | present along the wetland-upland transition zone, we buffered 5 m into | 52 | present along the wetland-upland transition zone, we buffered 5 m into | ||
| 53 | it. Open water and rice were excluded. If imagery was ambiguous, we | 53 | it. Open water and rice were excluded. If imagery was ambiguous, we | ||
| 54 | used Google Earth imagery from adjacent years to help distinguish if a | 54 | used Google Earth imagery from adjacent years to help distinguish if a | ||
| 55 | wetland was present. Each wetland\u2019s geomorphology was classified | 55 | wetland was present. Each wetland\u2019s geomorphology was classified | ||
| 56 | as slope (shallow hillside flow), pond fringe, fluvial, rice fringe, | 56 | as slope (shallow hillside flow), pond fringe, fluvial, rice fringe, | ||
| 57 | irrigation ditch, or waterfowl impoundment. We combined historic | 57 | irrigation ditch, or waterfowl impoundment. We combined historic | ||
| 58 | imagery and field data to determine the water sources. We surveyed 237 | 58 | imagery and field data to determine the water sources. We surveyed 237 | ||
| 59 | wetlands for occupancy of Black Rails up to three times each summer | 59 | wetlands for occupancy of Black Rails up to three times each summer | ||
| 60 | from 2012\u20132016 using established broadcast survey methods (for | 60 | from 2012\u20132016 using established broadcast survey methods (for | ||
| 61 | details see Richmond et al. 2010). To assess the effects of water | 61 | details see Richmond et al. 2010). To assess the effects of water | ||
| 62 | source on wetland hydrology, we resurveyed wetlands for 14 periods: in | 62 | source on wetland hydrology, we resurveyed wetlands for 14 periods: in | ||
| 63 | the early wet season (January 8\u201327), late wet season (March | 63 | the early wet season (January 8\u201327), late wet season (March | ||
| 64 | 22\u201325), early dry season (May 17\u2013June 20), and late dry | 64 | 22\u201325), early dry season (May 17\u2013June 20), and late dry | ||
| 65 | season (July 15\u2013August 15) from summer 2013\u20132016. At each | 65 | season (July 15\u2013August 15) from summer 2013\u20132016. At each | ||
| 66 | visit we walked throughout the wetland with a map of aerial imagery | 66 | visit we walked throughout the wetland with a map of aerial imagery | ||
| 67 | and recorded the percent wetness (areal percent of wetland saturated | 67 | and recorded the percent wetness (areal percent of wetland saturated | ||
| 68 | with water). We trapped mosquitoes at 63 wetlands from | 68 | with water). We trapped mosquitoes at 63 wetlands from | ||
| 69 | June\u2013October, 2012\u20132014 (4710 trap/nights) and estimated WNV | 69 | June\u2013October, 2012\u20132014 (4710 trap/nights) and estimated WNV | ||
| 70 | prevalence (probability of a mosquito testing positive for WNV) with | 70 | prevalence (probability of a mosquito testing positive for WNV) with | ||
| 71 | genetic testing. We estimated WNV transmission risk at each wetland as | 71 | genetic testing. We estimated WNV transmission risk at each wetland as | ||
| 72 | the mean abundance of WNV-infected Culex spp. (the main WNV vectors) | 72 | the mean abundance of WNV-infected Culex spp. (the main WNV vectors) | ||
| 73 | per trap/night. [Usage Notes] Note that wetland data is not a | 73 | per trap/night. [Usage Notes] Note that wetland data is not a | ||
| 74 | comprehensive list of all wetlands in the region. Missing values for | 74 | comprehensive list of all wetlands in the region. Missing values for | ||
| 75 | black rail occupancy in some years or visits within years are | 75 | black rail occupancy in some years or visits within years are | ||
| 76 | delineated with", | 76 | delineated with", | ||
| 77 | "es": "[Methods] We mapped all emergent wetlands > 5\u00d75 m | 77 | "es": "[Methods] We mapped all emergent wetlands > 5\u00d75 m | ||
| 78 | within our study area\u2014California\u2019s Sierra Nevada foothills | 78 | within our study area\u2014California\u2019s Sierra Nevada foothills | ||
| 79 | EPA zone III eco-region in Yuba, Nevada, and southern Butte countieso | 79 | EPA zone III eco-region in Yuba, Nevada, and southern Butte countieso | ||
| 80 | of California. Mapping was done by manually interpreting summer 2013 | 80 | of California. Mapping was done by manually interpreting summer 2013 | ||
| 81 | GeoEye-1 0.4 m imagery in Google Earth 7.1.5. Areas covered by | 81 | GeoEye-1 0.4 m imagery in Google Earth 7.1.5. Areas covered by | ||
| 82 | hydrophytes (Typha spp., Scirpus spp., Juncus effusus, Leersia | 82 | hydrophytes (Typha spp., Scirpus spp., Juncus effusus, Leersia | ||
| 83 | oryzoides, or various sedges) were considered wetland. We included | 83 | oryzoides, or various sedges) were considered wetland. We included | ||
| 84 | hydrophytes that appeared seasonally dried; if green vegetation was | 84 | hydrophytes that appeared seasonally dried; if green vegetation was | ||
| 85 | present along the wetland-upland transition zone, we buffered 5 m into | 85 | present along the wetland-upland transition zone, we buffered 5 m into | ||
| 86 | it. Open water and rice were excluded. If imagery was ambiguous, we | 86 | it. Open water and rice were excluded. If imagery was ambiguous, we | ||
| 87 | used Google Earth imagery from adjacent years to help distinguish if a | 87 | used Google Earth imagery from adjacent years to help distinguish if a | ||
| 88 | wetland was present. Each wetland\u2019s geomorphology was classified | 88 | wetland was present. Each wetland\u2019s geomorphology was classified | ||
| 89 | as slope (shallow hillside flow), pond fringe, fluvial, rice fringe, | 89 | as slope (shallow hillside flow), pond fringe, fluvial, rice fringe, | ||
| 90 | irrigation ditch, or waterfowl impoundment. We combined historic | 90 | irrigation ditch, or waterfowl impoundment. We combined historic | ||
| 91 | imagery and field data to determine the water sources. We surveyed 237 | 91 | imagery and field data to determine the water sources. We surveyed 237 | ||
| 92 | wetlands for occupancy of Black Rails up to three times each summer | 92 | wetlands for occupancy of Black Rails up to three times each summer | ||
| 93 | from 2012\u20132016 using established broadcast survey methods (for | 93 | from 2012\u20132016 using established broadcast survey methods (for | ||
| 94 | details see Richmond et al. 2010). To assess the effects of water | 94 | details see Richmond et al. 2010). To assess the effects of water | ||
| 95 | source on wetland hydrology, we resurveyed wetlands for 14 periods: in | 95 | source on wetland hydrology, we resurveyed wetlands for 14 periods: in | ||
| 96 | the early wet season (January 8\u201327), late wet season (March | 96 | the early wet season (January 8\u201327), late wet season (March | ||
| 97 | 22\u201325), early dry season (May 17\u2013June 20), and late dry | 97 | 22\u201325), early dry season (May 17\u2013June 20), and late dry | ||
| 98 | season (July 15\u2013August 15) from summer 2013\u20132016. At each | 98 | season (July 15\u2013August 15) from summer 2013\u20132016. At each | ||
| 99 | visit we walked throughout the wetland with a map of aerial imagery | 99 | visit we walked throughout the wetland with a map of aerial imagery | ||
| 100 | and recorded the percent wetness (areal percent of wetland saturated | 100 | and recorded the percent wetness (areal percent of wetland saturated | ||
| 101 | with water). We trapped mosquitoes at 63 wetlands from | 101 | with water). We trapped mosquitoes at 63 wetlands from | ||
| 102 | June\u2013October, 2012\u20132014 (4710 trap/nights) and estimated WNV | 102 | June\u2013October, 2012\u20132014 (4710 trap/nights) and estimated WNV | ||
| 103 | prevalence (probability of a mosquito testing positive for WNV) with | 103 | prevalence (probability of a mosquito testing positive for WNV) with | ||
| 104 | genetic testing. We estimated WNV transmission risk at each wetland as | 104 | genetic testing. We estimated WNV transmission risk at each wetland as | ||
| 105 | the mean abundance of WNV-infected Culex spp. (the main WNV vectors) | 105 | the mean abundance of WNV-infected Culex spp. (the main WNV vectors) | ||
| 106 | per trap/night. [Usage Notes] Note that wetland data is not a | 106 | per trap/night. [Usage Notes] Note that wetland data is not a | ||
| 107 | comprehensive list of all wetlands in the region. Missing values for | 107 | comprehensive list of all wetlands in the region. Missing values for | ||
| 108 | black rail occupancy in some years or visits within years are | 108 | black rail occupancy in some years or visits within years are | ||
| 109 | delineated with" | 109 | delineated with" | ||
| 110 | }, | 110 | }, | ||
| 111 | "groups": [ | 111 | "groups": [ | ||
| 112 | { | 112 | { | ||
| 113 | "description": "", | 113 | "description": "", | ||
| 114 | "display_name": "Ecolog\u00eda", | 114 | "display_name": "Ecolog\u00eda", | ||
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| 116 | "image_display_url": | 116 | "image_display_url": | ||
| 117 | atos.cchs.csic.es/uploads/group/2024-07-15-113023.996987Ecologia.png", | 117 | atos.cchs.csic.es/uploads/group/2024-07-15-113023.996987Ecologia.png", | ||
| 118 | "name": "ecologia", | 118 | "name": "ecologia", | ||
| 119 | "title": "Ecolog\u00eda" | 119 | "title": "Ecolog\u00eda" | ||
| 120 | } | 120 | } | ||
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| 123 | "identifier": "https://hdl.handle.net/10261/280602", | 123 | "identifier": "https://hdl.handle.net/10261/280602", | ||
| 124 | "instituto": [ | 124 | "instituto": [ | ||
| 125 | "Instituto de Pol\u00edticas y Bienes P\u00fablicos (IPP), CSIC" | 125 | "Instituto de Pol\u00edticas y Bienes P\u00fablicos (IPP), CSIC" | ||
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| 132 | "issued_date": "2021-04-22T00:00:00", | 132 | "issued_date": "2021-04-22T00:00:00", | ||
| 133 | "language": [ | 133 | "language": [ | ||
| 134 | "en" | 134 | "en" | ||
| 135 | ], | 135 | ], | ||
| 136 | "license_id": "https://creativecommons.org/publicdomain/zero/1.0/", | 136 | "license_id": "https://creativecommons.org/publicdomain/zero/1.0/", | ||
| 137 | "license_title": | 137 | "license_title": | ||
| 138 | "https://creativecommons.org/publicdomain/zero/1.0/", | 138 | "https://creativecommons.org/publicdomain/zero/1.0/", | ||
| 139 | "maintainer": null, | 139 | "maintainer": null, | ||
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| 141 | "metadata_created": "2024-05-30T14:40:36.232585", | 141 | "metadata_created": "2024-05-30T14:40:36.232585", | ||
| n | 142 | "metadata_modified": "2025-11-03T15:39:37.345984", | n | 142 | "metadata_modified": "2025-11-03T15:40:37.863961", |
| 143 | "multilingual_tags": { | 143 | "multilingual_tags": { | ||
| 144 | "en": [ | 144 | "en": [ | ||
| 145 | "Laterallus jamaicensis coturniculus", | 145 | "Laterallus jamaicensis coturniculus", | ||
| 146 | "California Black Rail", | 146 | "California Black Rail", | ||
| 147 | "Flaviviridae", | 147 | "Flaviviridae", | ||
| 148 | "Rangelands", | 148 | "Rangelands", | ||
| 149 | "Socio-ecological system", | 149 | "Socio-ecological system", | ||
| 150 | "Coupled human and natural system", | 150 | "Coupled human and natural system", | ||
| 151 | "Coupled natural-human system", | 151 | "Coupled natural-human system", | ||
| 152 | "Metapopulation", | 152 | "Metapopulation", | ||
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