Changes
On April 16, 2025 at 6:58:10 AM UTC,

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Moved Assessing impacts of social-ecological diversity on resilience in a wetland coupled human and natural system: Data release from organization Instituto de Políticas y Bienes Públicos (IPP), CSIC to organization Agencia Estatal Consejo Superior de Investigaciones Científicas (CSIC)
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 | }, | ||
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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" | ||
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123 | "identifier": "http://hdl.handle.net/10261/280602", | 123 | "identifier": "http://hdl.handle.net/10261/280602", | ||
n | n | 124 | "instituto": [ | ||
125 | "Instituto de Pol\u00edticas y Bienes P\u00fablicos (IPP), CSIC" | ||||
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129 | "issued_date": "2021-04-22T00:00:00", | 132 | "issued_date": "2021-04-22T00:00:00", | ||
130 | "language": [ | 133 | "language": [ | ||
131 | "en" | 134 | "en" | ||
132 | ], | 135 | ], | ||
133 | "license_id": "https://creativecommons.org/publicdomain/zero/1.0/", | 136 | "license_id": "https://creativecommons.org/publicdomain/zero/1.0/", | ||
134 | "license_title": | 137 | "license_title": | ||
135 | "https://creativecommons.org/publicdomain/zero/1.0/", | 138 | "https://creativecommons.org/publicdomain/zero/1.0/", | ||
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137 | "maintainer_email": null, | 140 | "maintainer_email": null, | ||
138 | "metadata_created": "2024-05-30T14:40:36.232585", | 141 | "metadata_created": "2024-05-30T14:40:36.232585", | ||
n | 139 | "metadata_modified": "2025-03-13T12:20:46.387029", | n | 142 | "metadata_modified": "2025-04-16T06:58:10.385155", |
140 | "multilingual_tags": { | 143 | "multilingual_tags": { | ||
141 | "en": [ | 144 | "en": [ | ||
142 | "Laterallus jamaicensis coturniculus", | 145 | "Laterallus jamaicensis coturniculus", | ||
143 | "California Black Rail", | 146 | "California Black Rail", | ||
144 | "Flaviviridae", | 147 | "Flaviviridae", | ||
145 | "Rangelands", | 148 | "Rangelands", | ||
146 | "Socio-ecological system", | 149 | "Socio-ecological system", | ||
147 | "Coupled human and natural system", | 150 | "Coupled human and natural system", | ||
148 | "Coupled natural-human system", | 151 | "Coupled natural-human system", | ||
149 | "Metapopulation", | 152 | "Metapopulation", | ||
150 | "Earth and related environmental sciences" | 153 | "Earth and related environmental sciences" | ||
151 | ] | 154 | ] | ||
152 | }, | 155 | }, | ||
153 | "name": | 156 | "name": | ||
154 | -ecological-diversity-on-resilience-in-a-wetland-coupled-human-and-n", | 157 | -ecological-diversity-on-resilience-in-a-wetland-coupled-human-and-n", | ||
155 | "notes": null, | 158 | "notes": null, | ||
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157 | "num_tags": 0, | 160 | "num_tags": 0, | ||
158 | "organization": { | 161 | "organization": { | ||
159 | "approval_status": "approved", | 162 | "approval_status": "approved", | ||
n | 160 | "created": "2023-09-25T13:00:48.436872", | n | 163 | "created": "2025-04-15T15:18:43.186369", |
161 | "description": "El Instituto de Pol\u00edticas y Bienes | 164 | "description": "", | ||
162 | P\u00fablicos (IPP) es un instituto del CSIC que se cre\u00f3 en 2007, | 165 | "id": "e0fb512f-fa1e-43d9-ba1e-22b1f834702e", | ||
163 | con el objetivo de generar investigaci\u00f3n cient\u00edfica de | ||||
164 | excelencia internacional y de gran impacto social en el \u00e1mbito | ||||
165 | del an\u00e1lisis de las pol\u00edticas p\u00fablicas. \r\n\r\nEl IPP | ||||
166 | tiene como misi\u00f3n la generaci\u00f3n de conocimiento | ||||
167 | cient\u00edfico en torno al an\u00e1lisis de pol\u00edticas y bienes | ||||
168 | p\u00fablicos, as\u00ed como su gesti\u00f3n por medio de | ||||
169 | organizaciones privadas, instituciones p\u00fablicas y otros actores | ||||
170 | sociales.", | ||||
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175 | "state": "active", | 170 | "state": "active", | ||
n | 176 | "title": "Instituto de Pol\u00edticas y Bienes P\u00fablicos | n | 171 | "title": "Agencia Estatal Consejo Superior de Investigaciones |
177 | (IPP), CSIC", | 172 | Cient\u00edficas (CSIC)", | ||
178 | "type": "organization" | 173 | "type": "organization" | ||
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