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en Assessing impacts of social-ecological diversity on resilience in a wetland coupled human and natural system: Data release -
Modificado el valor del campo
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a{'en': '[Methods] We mapped all emergent wetlands > 5×5 m within our study area—California’s Sierra Nevada foothills EPA zone III eco-region in Yuba, Nevada, and southern Butte countieso of California. Mapping was done by manually interpreting summer 2013 GeoEye-1 0.4 m imagery in Google Earth 7.1.5. Areas covered by hydrophytes (Typha spp., Scirpus spp., Juncus effusus, Leersia oryzoides, or various sedges) were considered wetland. We included hydrophytes that appeared seasonally dried; if green vegetation was present along the wetland-upland transition zone, we buffered 5 m into it. Open water and rice were excluded. If imagery was ambiguous, we used Google Earth imagery from adjacent years to help distinguish if a wetland was present. Each wetland’s geomorphology was classified as slope (shallow hillside flow), pond fringe, fluvial, rice fringe, irrigation ditch, or waterfowl impoundment. We combined historic imagery and field data to determine the water sources. We surveyed 237 wetlands for occupancy of Black Rails up to three times each summer from 2012–2016 using established broadcast survey methods (for details see Richmond et al. 2010). To assess the effects of water source on wetland hydrology, we resurveyed wetlands for 14 periods: in the early wet season (January 8–27), late wet season (March 22–25), early dry season (May 17–June 20), and late dry season (July 15–August 15) from summer 2013–2016. At each visit we walked throughout the wetland with a map of aerial imagery and recorded the percent wetness (areal percent of wetland saturated with water). We trapped mosquitoes at 63 wetlands from June–October, 2012–2014 (4710 trap/nights) and estimated WNV prevalence (probability of a mosquito testing positive for WNV) with genetic testing. We estimated WNV transmission risk at each wetland as the mean abundance of WNV-infected Culex spp. (the main WNV vectors) per trap/night. [Usage Notes] Note that wetland data is not a comprehensive list of all wetlands in the region. Missing values for black rail occupancy in some years or visits within years are delineated with', 'es': '[Methods] We mapped all emergent wetlands > 5×5 m within our study area—California’s Sierra Nevada foothills EPA zone III eco-region in Yuba, Nevada, and southern Butte countieso of California. Mapping was done by manually interpreting summer 2013 GeoEye-1 0.4 m imagery in Google Earth 7.1.5. Areas covered by hydrophytes (Typha spp., Scirpus spp., Juncus effusus, Leersia oryzoides, or various sedges) were considered wetland. We included hydrophytes that appeared seasonally dried; if green vegetation was present along the wetland-upland transition zone, we buffered 5 m into it. Open water and rice were excluded. If imagery was ambiguous, we used Google Earth imagery from adjacent years to help distinguish if a wetland was present. Each wetland’s geomorphology was classified as slope (shallow hillside flow), pond fringe, fluvial, rice fringe, irrigation ditch, or waterfowl impoundment. We combined historic imagery and field data to determine the water sources. We surveyed 237 wetlands for occupancy of Black Rails up to three times each summer from 2012–2016 using established broadcast survey methods (for details see Richmond et al. 2010). To assess the effects of water source on wetland hydrology, we resurveyed wetlands for 14 periods: in the early wet season (January 8–27), late wet season (March 22–25), early dry season (May 17–June 20), and late dry season (July 15–August 15) from summer 2013–2016. At each visit we walked throughout the wetland with a map of aerial imagery and recorded the percent wetness (areal percent of wetland saturated with water). We trapped mosquitoes at 63 wetlands from June–October, 2012–2014 (4710 trap/nights) and estimated WNV prevalence (probability of a mosquito testing positive for WNV) with genetic testing. We estimated WNV transmission risk at each wetland as the mean abundance of WNV-infected Culex spp. (the main WNV vectors) per trap/night. [Usage Notes] Note that wetland data is not a comprehensive list of all wetlands in the region. Missing values for black rail occupancy in some years or visits within years are delineated with'}
en Assessing impacts of social-ecological diversity on resilience in a wetland coupled human and natural system: Data release
f | 1 | { | f | 1 | { |
n | n | 2 | "Observaciones": { | ||
3 | "en": "", | ||||
4 | "es": "Van Schmidt, Nathan D.; Oviedo, Jos\u00e9 L.; Hruska, | ||||
5 | Tracy; Huntsinger, Lynn; Kovach, Tony; Kilpatrick, A. Marm; Miller, | ||||
6 | Norman L.; Beissinger, Steven R.; 2021; Assessing impacts of | ||||
7 | social-ecological diversity on resilience in a wetland coupled human | ||||
8 | and natural system: Data release [Dataset]; Dryad; Version 4; | ||||
9 | https://doi.org/10.6078/D1970G" | ||||
10 | }, | ||||
2 | "author": null, | 11 | "author": null, | ||
3 | "author_email": null, | 12 | "author_email": null, | ||
n | n | 13 | "autor": { | ||
14 | "es": [ | ||||
15 | "Nathan D. Van Schmidt", | ||||
16 | "Jos\u00e9 L. Oviedo", | ||||
17 | "Tracy Hruska", | ||||
18 | "Lynn Huntsinger", | ||||
19 | "Tony Kovach", | ||||
20 | "A. Marm Kilpatrick", | ||||
21 | "Norman L. Miller", | ||||
22 | "Steven R. Beissinger" | ||||
23 | ] | ||||
24 | }, | ||||
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7 | "description": { | 28 | "description": { | ||
n | 8 | "en": "Theory posits that resilience of ecosystems increases when | n | 29 | "en": "[Methods] We mapped all emergent wetlands > 5\u00d75 m |
9 | there is a diversity of agents (e.g., species) and linkages between | 30 | within our study area\u2014California\u2019s Sierra Nevada foothills | ||
10 | them. If ecosystems are conceptualized as components of \u201ccoupled | 31 | EPA zone III eco-region in Yuba, Nevada, and southern Butte countieso | ||
11 | human and natural systems\u201d, then a corollary would be that novel | 32 | of California. Mapping was done by manually interpreting summer 2013 | ||
12 | types of human-induced diversity may also foster resilience. We | 33 | GeoEye-1 0.4 m imagery in Google Earth 7.1.5. Areas covered by | ||
13 | explored this hypothesis by studying how socially created diversity | 34 | hydrophytes (Typha spp., Scirpus spp., Juncus effusus, Leersia | ||
14 | mediated the impact of a historically severe drought on a network of | 35 | oryzoides, or various sedges) were considered wetland. We included | ||
15 | wetlands in the foothills of the California Sierra Nevada containing a | 36 | hydrophytes that appeared seasonally dried; if green vegetation was | ||
16 | metapopulation of the threatened California Black Rail (Laterallus | 37 | present along the wetland-upland transition zone, we buffered 5 m into | ||
17 | jamaicensis coturniculus). We examined how (1) diversity in | 38 | it. Open water and rice were excluded. If imagery was ambiguous, we | ||
18 | motivations for land ownership affected use of irrigation water and | 39 | used Google Earth imagery from adjacent years to help distinguish if a | ||
19 | response to drought, (2) differences in natural and irrigated water | 40 | wetland was present. Each wetland\u2019s geomorphology was classified | ||
20 | sources affected wetland drying in response to drought, and (3) these | 41 | as slope (shallow hillside flow), pond fringe, fluvial, rice fringe, | ||
21 | processes affected the persistence of rails and the transmission risk | 42 | irrigation ditch, or waterfowl impoundment. We combined historic | ||
22 | of West Nile virus, an emerging infectious disease that threatens | 43 | imagery and field data to determine the water sources. We surveyed 237 | ||
23 | people and rails. Wetlands were mostly fed by inefficiencies and leaks | 44 | wetlands for occupancy of Black Rails up to three times each summer | ||
24 | from the irrigation system. Wetlands with both natural and irrigated | 45 | from 2012\u20132016 using established broadcast survey methods (for | ||
25 | water sources were larger, wetter, and likelier to persist through | 46 | details see Richmond et al. 2010). To assess the effects of water | ||
26 | drought because these two sources showed response diversity by drying | 47 | source on wetland hydrology, we resurveyed wetlands for 14 periods: in | ||
27 | at different times. Wetlands with diverse water sources also provided | 48 | the early wet season (January 8\u201327), late wet season (March | ||
28 | the best habitat for the California Black Rail, and irrigation | 49 | 22\u201325), early dry season (May 17\u2013June 20), and late dry | ||
29 | appeared responsible for its persistence through the drought. | 50 | season (July 15\u2013August 15) from summer 2013\u20132016. At each | ||
30 | Irrigation increased WNV transmission risk by increasing the quantity, | 51 | visit we walked throughout the wetland with a map of aerial imagery | ||
31 | but not the quality, of wetland habitats for mosquitoes. The impacts | 52 | and recorded the percent wetness (areal percent of wetland saturated | ||
32 | of social diversity were more ambiguous, with redundancy prevalent. | 53 | with water). We trapped mosquitoes at 63 wetlands from | ||
33 | However, profit-motivated landowners provided wetlands more irrigation | 54 | June\u2013October, 2012\u20132014 (4710 trap/nights) and estimated WNV | ||
34 | during non-drought conditions, while other landowner types were more | 55 | prevalence (probability of a mosquito testing positive for WNV) with | ||
35 | likely to continue providing irrigation during drought. This dataset | 56 | genetic testing. We estimated WNV transmission risk at each wetland as | ||
36 | provides the wetland, California Black Rail, and West Nile virus data | 57 | the mean abundance of WNV-infected Culex spp. (the main WNV vectors) | ||
37 | that support the findings of this study. Partial social and geospatial | 58 | per trap/night. [Usage Notes] Note that wetland data is not a | ||
38 | data are available by emailing the first author upon request, | 59 | comprehensive list of all wetlands in the region. Missing values for | ||
39 | excluding some information that would make respondents identifiable.", | 60 | black rail occupancy in some years or visits within years are | ||
40 | "es": "Theory posits that resilience of ecosystems increases when | 61 | delineated with", | ||
41 | there is a diversity of agents (e.g., species) and linkages between | 62 | "es": "[Methods] We mapped all emergent wetlands > 5\u00d75 m | ||
42 | them. If ecosystems are conceptualized as components of \u201ccoupled | 63 | within our study area\u2014California\u2019s Sierra Nevada foothills | ||
43 | human and natural systems\u201d, then a corollary would be that novel | 64 | EPA zone III eco-region in Yuba, Nevada, and southern Butte countieso | ||
44 | types of human-induced diversity may also foster resilience. We | 65 | of California. Mapping was done by manually interpreting summer 2013 | ||
45 | explored this hypothesis by studying how socially created diversity | 66 | GeoEye-1 0.4 m imagery in Google Earth 7.1.5. Areas covered by | ||
46 | mediated the impact of a historically severe drought on a network of | 67 | hydrophytes (Typha spp., Scirpus spp., Juncus effusus, Leersia | ||
47 | wetlands in the foothills of the California Sierra Nevada containing a | 68 | oryzoides, or various sedges) were considered wetland. We included | ||
48 | metapopulation of the threatened California Black Rail (Laterallus | 69 | hydrophytes that appeared seasonally dried; if green vegetation was | ||
49 | jamaicensis coturniculus). We examined how (1) diversity in | 70 | present along the wetland-upland transition zone, we buffered 5 m into | ||
50 | motivations for land ownership affected use of irrigation water and | 71 | it. Open water and rice were excluded. If imagery was ambiguous, we | ||
51 | response to drought, (2) differences in natural and irrigated water | 72 | used Google Earth imagery from adjacent years to help distinguish if a | ||
52 | sources affected wetland drying in response to drought, and (3) these | 73 | wetland was present. Each wetland\u2019s geomorphology was classified | ||
53 | processes affected the persistence of rails and the transmission risk | 74 | as slope (shallow hillside flow), pond fringe, fluvial, rice fringe, | ||
54 | of West Nile virus, an emerging infectious disease that threatens | 75 | irrigation ditch, or waterfowl impoundment. We combined historic | ||
55 | people and rails. Wetlands were mostly fed by inefficiencies and leaks | 76 | imagery and field data to determine the water sources. We surveyed 237 | ||
56 | from the irrigation system. Wetlands with both natural and irrigated | 77 | wetlands for occupancy of Black Rails up to three times each summer | ||
57 | water sources were larger, wetter, and likelier to persist through | 78 | from 2012\u20132016 using established broadcast survey methods (for | ||
58 | drought because these two sources showed response diversity by drying | 79 | details see Richmond et al. 2010). To assess the effects of water | ||
59 | at different times. Wetlands with diverse water sources also provided | 80 | source on wetland hydrology, we resurveyed wetlands for 14 periods: in | ||
60 | the best habitat for the California Black Rail, and irrigation | 81 | the early wet season (January 8\u201327), late wet season (March | ||
61 | appeared responsible for its persistence through the drought. | 82 | 22\u201325), early dry season (May 17\u2013June 20), and late dry | ||
62 | Irrigation increased WNV transmission risk by increasing the quantity, | 83 | season (July 15\u2013August 15) from summer 2013\u20132016. At each | ||
63 | but not the quality, of wetland habitats for mosquitoes. The impacts | 84 | visit we walked throughout the wetland with a map of aerial imagery | ||
64 | of social diversity were more ambiguous, with redundancy prevalent. | 85 | and recorded the percent wetness (areal percent of wetland saturated | ||
65 | However, profit-motivated landowners provided wetlands more irrigation | 86 | with water). We trapped mosquitoes at 63 wetlands from | ||
66 | during non-drought conditions, while other landowner types were more | 87 | June\u2013October, 2012\u20132014 (4710 trap/nights) and estimated WNV | ||
67 | likely to continue providing irrigation during drought. This dataset | 88 | prevalence (probability of a mosquito testing positive for WNV) with | ||
68 | provides the wetland, California Black Rail, and West Nile virus data | 89 | genetic testing. We estimated WNV transmission risk at each wetland as | ||
69 | that support the findings of this study. Partial social and geospatial | 90 | the mean abundance of WNV-infected Culex spp. (the main WNV vectors) | ||
70 | data are available by emailing the first author upon request, | 91 | per trap/night. [Usage Notes] Note that wetland data is not a | ||
71 | excluding some information that would make respondents identifiable." | 92 | comprehensive list of all wetlands in the region. Missing values for | ||
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