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En el instante 30 de mayo de 2024, 14:40:51 UTC, Administrador CKAN:
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Añadido recurso WNV_Prevalence_Data.csv a Assessing impacts of social-ecological diversity on resilience in a wetland coupled human and natural system: Data release
f | 1 | { | f | 1 | { |
2 | "author": null, | 2 | "author": null, | ||
3 | "author_email": null, | 3 | "author_email": null, | ||
4 | "conforms_to": [], | 4 | "conforms_to": [], | ||
5 | "coverage_new": {}, | 5 | "coverage_new": {}, | ||
6 | "creator_user_id": "196556b3-e0c4-4c51-a9e6-f51cc752bc37", | 6 | "creator_user_id": "196556b3-e0c4-4c51-a9e6-f51cc752bc37", | ||
7 | "description": { | 7 | "description": { | ||
8 | "en": "Theory posits that resilience of ecosystems increases when | 8 | "en": "Theory posits that resilience of ecosystems increases when | ||
9 | there is a diversity of agents (e.g., species) and linkages between | 9 | there is a diversity of agents (e.g., species) and linkages between | ||
10 | them. If ecosystems are conceptualized as components of \u201ccoupled | 10 | them. If ecosystems are conceptualized as components of \u201ccoupled | ||
11 | human and natural systems\u201d, then a corollary would be that novel | 11 | human and natural systems\u201d, then a corollary would be that novel | ||
12 | types of human-induced diversity may also foster resilience. We | 12 | types of human-induced diversity may also foster resilience. We | ||
13 | explored this hypothesis by studying how socially created diversity | 13 | explored this hypothesis by studying how socially created diversity | ||
14 | mediated the impact of a historically severe drought on a network of | 14 | mediated the impact of a historically severe drought on a network of | ||
15 | wetlands in the foothills of the California Sierra Nevada containing a | 15 | wetlands in the foothills of the California Sierra Nevada containing a | ||
16 | metapopulation of the threatened California Black Rail (Laterallus | 16 | metapopulation of the threatened California Black Rail (Laterallus | ||
17 | jamaicensis coturniculus). We examined how (1) diversity in | 17 | jamaicensis coturniculus). We examined how (1) diversity in | ||
18 | motivations for land ownership affected use of irrigation water and | 18 | motivations for land ownership affected use of irrigation water and | ||
19 | response to drought, (2) differences in natural and irrigated water | 19 | response to drought, (2) differences in natural and irrigated water | ||
20 | sources affected wetland drying in response to drought, and (3) these | 20 | sources affected wetland drying in response to drought, and (3) these | ||
21 | processes affected the persistence of rails and the transmission risk | 21 | processes affected the persistence of rails and the transmission risk | ||
22 | of West Nile virus, an emerging infectious disease that threatens | 22 | of West Nile virus, an emerging infectious disease that threatens | ||
23 | people and rails. Wetlands were mostly fed by inefficiencies and leaks | 23 | people and rails. Wetlands were mostly fed by inefficiencies and leaks | ||
24 | from the irrigation system. Wetlands with both natural and irrigated | 24 | from the irrigation system. Wetlands with both natural and irrigated | ||
25 | water sources were larger, wetter, and likelier to persist through | 25 | water sources were larger, wetter, and likelier to persist through | ||
26 | drought because these two sources showed response diversity by drying | 26 | drought because these two sources showed response diversity by drying | ||
27 | at different times. Wetlands with diverse water sources also provided | 27 | at different times. Wetlands with diverse water sources also provided | ||
28 | the best habitat for the California Black Rail, and irrigation | 28 | the best habitat for the California Black Rail, and irrigation | ||
29 | appeared responsible for its persistence through the drought. | 29 | appeared responsible for its persistence through the drought. | ||
30 | Irrigation increased WNV transmission risk by increasing the quantity, | 30 | Irrigation increased WNV transmission risk by increasing the quantity, | ||
31 | but not the quality, of wetland habitats for mosquitoes. The impacts | 31 | but not the quality, of wetland habitats for mosquitoes. The impacts | ||
32 | of social diversity were more ambiguous, with redundancy prevalent. | 32 | of social diversity were more ambiguous, with redundancy prevalent. | ||
33 | However, profit-motivated landowners provided wetlands more irrigation | 33 | However, profit-motivated landowners provided wetlands more irrigation | ||
34 | during non-drought conditions, while other landowner types were more | 34 | during non-drought conditions, while other landowner types were more | ||
35 | likely to continue providing irrigation during drought. This dataset | 35 | likely to continue providing irrigation during drought. This dataset | ||
36 | provides the wetland, California Black Rail, and West Nile virus data | 36 | provides the wetland, California Black Rail, and West Nile virus data | ||
37 | that support the findings of this study. Partial social and geospatial | 37 | that support the findings of this study. Partial social and geospatial | ||
38 | data are available by emailing the first author upon request, | 38 | data are available by emailing the first author upon request, | ||
39 | excluding some information that would make respondents identifiable.", | 39 | excluding some information that would make respondents identifiable.", | ||
40 | "es": "Theory posits that resilience of ecosystems increases when | 40 | "es": "Theory posits that resilience of ecosystems increases when | ||
41 | there is a diversity of agents (e.g., species) and linkages between | 41 | there is a diversity of agents (e.g., species) and linkages between | ||
42 | them. If ecosystems are conceptualized as components of \u201ccoupled | 42 | them. If ecosystems are conceptualized as components of \u201ccoupled | ||
43 | human and natural systems\u201d, then a corollary would be that novel | 43 | human and natural systems\u201d, then a corollary would be that novel | ||
44 | types of human-induced diversity may also foster resilience. We | 44 | types of human-induced diversity may also foster resilience. We | ||
45 | explored this hypothesis by studying how socially created diversity | 45 | explored this hypothesis by studying how socially created diversity | ||
46 | mediated the impact of a historically severe drought on a network of | 46 | mediated the impact of a historically severe drought on a network of | ||
47 | wetlands in the foothills of the California Sierra Nevada containing a | 47 | wetlands in the foothills of the California Sierra Nevada containing a | ||
48 | metapopulation of the threatened California Black Rail (Laterallus | 48 | metapopulation of the threatened California Black Rail (Laterallus | ||
49 | jamaicensis coturniculus). We examined how (1) diversity in | 49 | jamaicensis coturniculus). We examined how (1) diversity in | ||
50 | motivations for land ownership affected use of irrigation water and | 50 | motivations for land ownership affected use of irrigation water and | ||
51 | response to drought, (2) differences in natural and irrigated water | 51 | response to drought, (2) differences in natural and irrigated water | ||
52 | sources affected wetland drying in response to drought, and (3) these | 52 | sources affected wetland drying in response to drought, and (3) these | ||
53 | processes affected the persistence of rails and the transmission risk | 53 | processes affected the persistence of rails and the transmission risk | ||
54 | of West Nile virus, an emerging infectious disease that threatens | 54 | of West Nile virus, an emerging infectious disease that threatens | ||
55 | people and rails. Wetlands were mostly fed by inefficiencies and leaks | 55 | people and rails. Wetlands were mostly fed by inefficiencies and leaks | ||
56 | from the irrigation system. Wetlands with both natural and irrigated | 56 | from the irrigation system. Wetlands with both natural and irrigated | ||
57 | water sources were larger, wetter, and likelier to persist through | 57 | water sources were larger, wetter, and likelier to persist through | ||
58 | drought because these two sources showed response diversity by drying | 58 | drought because these two sources showed response diversity by drying | ||
59 | at different times. Wetlands with diverse water sources also provided | 59 | at different times. Wetlands with diverse water sources also provided | ||
60 | the best habitat for the California Black Rail, and irrigation | 60 | the best habitat for the California Black Rail, and irrigation | ||
61 | appeared responsible for its persistence through the drought. | 61 | appeared responsible for its persistence through the drought. | ||
62 | Irrigation increased WNV transmission risk by increasing the quantity, | 62 | Irrigation increased WNV transmission risk by increasing the quantity, | ||
63 | but not the quality, of wetland habitats for mosquitoes. The impacts | 63 | but not the quality, of wetland habitats for mosquitoes. The impacts | ||
64 | of social diversity were more ambiguous, with redundancy prevalent. | 64 | of social diversity were more ambiguous, with redundancy prevalent. | ||
65 | However, profit-motivated landowners provided wetlands more irrigation | 65 | However, profit-motivated landowners provided wetlands more irrigation | ||
66 | during non-drought conditions, while other landowner types were more | 66 | during non-drought conditions, while other landowner types were more | ||
67 | likely to continue providing irrigation during drought. This dataset | 67 | likely to continue providing irrigation during drought. This dataset | ||
68 | provides the wetland, California Black Rail, and West Nile virus data | 68 | provides the wetland, California Black Rail, and West Nile virus data | ||
69 | that support the findings of this study. Partial social and geospatial | 69 | that support the findings of this study. Partial social and geospatial | ||
70 | data are available by emailing the first author upon request, | 70 | data are available by emailing the first author upon request, | ||
71 | excluding some information that would make respondents identifiable." | 71 | excluding some information that would make respondents identifiable." | ||
72 | }, | 72 | }, | ||
73 | "groups": [], | 73 | "groups": [], | ||
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75 | "identifier": "http://hdl.handle.net/10261/280602", | 75 | "identifier": "http://hdl.handle.net/10261/280602", | ||
76 | "isopen": false, | 76 | "isopen": false, | ||
77 | "issued_date": "2021-04-21T00:00:00", | 77 | "issued_date": "2021-04-21T00:00:00", | ||
78 | "language": [ | 78 | "language": [ | ||
79 | "en" | 79 | "en" | ||
80 | ], | 80 | ], | ||
81 | "license_id": "https://creativecommons.org/publicdomain/zero/1.0/", | 81 | "license_id": "https://creativecommons.org/publicdomain/zero/1.0/", | ||
82 | "license_title": | 82 | "license_title": | ||
83 | "https://creativecommons.org/publicdomain/zero/1.0/", | 83 | "https://creativecommons.org/publicdomain/zero/1.0/", | ||
84 | "maintainer": null, | 84 | "maintainer": null, | ||
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86 | "metadata_created": "2024-05-30T14:40:36.232585", | 86 | "metadata_created": "2024-05-30T14:40:36.232585", | ||
n | 87 | "metadata_modified": "2024-05-30T14:40:36.232589", | n | 87 | "metadata_modified": "2024-05-30T14:40:51.052003", |
88 | "multilingual_tags": { | 88 | "multilingual_tags": { | ||
89 | "en": [ | 89 | "en": [ | ||
90 | "Laterallus jamaicensis coturniculus", | 90 | "Laterallus jamaicensis coturniculus", | ||
91 | "California Black Rail", | 91 | "California Black Rail", | ||
92 | "Flaviviridae", | 92 | "Flaviviridae", | ||
93 | "Rangelands", | 93 | "Rangelands", | ||
94 | "Socio-ecological system", | 94 | "Socio-ecological system", | ||
95 | "Coupled human and natural system", | 95 | "Coupled human and natural system", | ||
96 | "Coupled natural-human system", | 96 | "Coupled natural-human system", | ||
97 | "Metapopulation", | 97 | "Metapopulation", | ||
98 | "Earth and related environmental sciences" | 98 | "Earth and related environmental sciences" | ||
99 | ], | 99 | ], | ||
100 | "es": [ | 100 | "es": [ | ||
101 | "Laterallus jamaicensis coturniculus", | 101 | "Laterallus jamaicensis coturniculus", | ||
102 | "California Black Rail", | 102 | "California Black Rail", | ||
103 | "Flaviviridae", | 103 | "Flaviviridae", | ||
104 | "Rangelands", | 104 | "Rangelands", | ||
105 | "Socio-ecological system", | 105 | "Socio-ecological system", | ||
106 | "Coupled human and natural system", | 106 | "Coupled human and natural system", | ||
107 | "Coupled natural-human system", | 107 | "Coupled natural-human system", | ||
108 | "Metapopulation", | 108 | "Metapopulation", | ||
109 | "Earth and related environmental sciences" | 109 | "Earth and related environmental sciences" | ||
110 | ] | 110 | ] | ||
111 | }, | 111 | }, | ||
112 | "name": | 112 | "name": | ||
113 | -ecological-diversity-on-resilience-in-a-wetland-coupled-human-and-n", | 113 | -ecological-diversity-on-resilience-in-a-wetland-coupled-human-and-n", | ||
114 | "notes": null, | 114 | "notes": null, | ||
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118 | "approval_status": "approved", | 118 | "approval_status": "approved", | ||
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121 | P\u00fablicos (IPP) es un instituto del CSIC que se cre\u00f3 en 2007, | 121 | P\u00fablicos (IPP) es un instituto del CSIC que se cre\u00f3 en 2007, | ||
122 | con el objetivo de generar investigaci\u00f3n cient\u00edfica de | 122 | con el objetivo de generar investigaci\u00f3n cient\u00edfica de | ||
123 | excelencia internacional y de gran impacto social en el \u00e1mbito | 123 | excelencia internacional y de gran impacto social en el \u00e1mbito | ||
124 | del an\u00e1lisis de las pol\u00edticas p\u00fablicas. \r\n\r\nEl IPP | 124 | del an\u00e1lisis de las pol\u00edticas p\u00fablicas. \r\n\r\nEl IPP | ||
125 | tiene como misi\u00f3n la generaci\u00f3n de conocimiento | 125 | tiene como misi\u00f3n la generaci\u00f3n de conocimiento | ||
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159 | "title": "Assessing impacts of social-ecological diversity on | 191 | "title": "Assessing impacts of social-ecological diversity on | ||
160 | resilience in a wetland coupled human and natural system: Data | 192 | resilience in a wetland coupled human and natural system: Data | ||
161 | release", | 193 | release", | ||
162 | "title_translated": { | 194 | "title_translated": { | ||
163 | "en": "Assessing impacts of social-ecological diversity on | 195 | "en": "Assessing impacts of social-ecological diversity on | ||
164 | resilience in a wetland coupled human and natural system: Data | 196 | resilience in a wetland coupled human and natural system: Data | ||
165 | release", | 197 | release", | ||
166 | "es": "Assessing impacts of social-ecological diversity on | 198 | "es": "Assessing impacts of social-ecological diversity on | ||
167 | resilience in a wetland coupled human and natural system: Data | 199 | resilience in a wetland coupled human and natural system: Data | ||
168 | release" | 200 | release" | ||
169 | }, | 201 | }, | ||
170 | "type": "dataset", | 202 | "type": "dataset", | ||
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172 | "version": null | 204 | "version": null | ||
173 | } | 205 | } |