Changes
On August 17, 2021 at 11:22:02 AM UTC, Felix Neff:
-
Changed value of field
related_publications
to* Neff, F., Resch, M. C., Marty, A., Rolley, J. D., Schütz, M., Risch, A. C., & Gossner, M. M. (2020). Long‐term restoration success of insect herbivore communities in semi‐natural grasslands: a functional approach. Ecological Applications, 30(6), e02133 (12 pp.). https://www.dora.lib4ri.ch/wsl/islandora/object/wsl:23144 * wsl:23144
in Grassland restoration: insects and insect traits
f | 1 | { | f | 1 | { |
2 | "author": "[{\"affiliation\": \"WSL\", \"affiliation_02\": \"ETH\", | 2 | "author": "[{\"affiliation\": \"WSL\", \"affiliation_02\": \"ETH\", | ||
3 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | 3 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | ||
4 | \"validation\", \"curation\", \"software\", \"publication\"], | 4 | \"validation\", \"curation\", \"software\", \"publication\"], | ||
5 | \"email\": \"felix.neff@wsl.ch\", \"given_name\": \"Felix\", | 5 | \"email\": \"felix.neff@wsl.ch\", \"given_name\": \"Felix\", | ||
6 | \"identifier\": \"0000-0001-7266-2589\", \"name\": \"Neff\"}, | 6 | \"identifier\": \"0000-0001-7266-2589\", \"name\": \"Neff\"}, | ||
7 | {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | 7 | {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | ||
8 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | 8 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | ||
9 | \"validation\", \"curation\", \"software\", \"publication\"], | 9 | \"validation\", \"curation\", \"software\", \"publication\"], | ||
10 | \"email\": \"carol.resch@wsl.ch\", \"given_name\": \"M. Carol\", | 10 | \"email\": \"carol.resch@wsl.ch\", \"given_name\": \"M. Carol\", | ||
11 | \"identifier\": \"0000-0003-1067-1142\", \"name\": \"Resch\"}, | 11 | \"identifier\": \"0000-0003-1067-1142\", \"name\": \"Resch\"}, | ||
12 | {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | 12 | {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | ||
13 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | 13 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | ||
14 | \"publication\"], \"email\": \"anja.marty@wsl.ch\", \"given_name\": | 14 | \"publication\"], \"email\": \"anja.marty@wsl.ch\", \"given_name\": | ||
15 | \"Anja\", \"identifier\": \"\", \"name\": \"Marty\"}, | 15 | \"Anja\", \"identifier\": \"\", \"name\": \"Marty\"}, | ||
16 | {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | 16 | {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | ||
17 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | 17 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | ||
18 | \"publication\"], \"email\": \"jacob.rolley@wsl.ch\", \"given_name\": | 18 | \"publication\"], \"email\": \"jacob.rolley@wsl.ch\", \"given_name\": | ||
19 | \"Jacob D.\", \"identifier\": \"\", \"name\": \"Rolley\"}, | 19 | \"Jacob D.\", \"identifier\": \"\", \"name\": \"Rolley\"}, | ||
20 | {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | 20 | {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | ||
21 | \"affiliation_03\": \"\", \"data_credit\": [\"publication\", | 21 | \"affiliation_03\": \"\", \"data_credit\": [\"publication\", | ||
22 | \"supervision\"], \"email\": \"martin.schuetz@wsl.ch\", | 22 | \"supervision\"], \"email\": \"martin.schuetz@wsl.ch\", | ||
23 | \"given_name\": \"Martin\", \"identifier\": \"\", \"name\": | 23 | \"given_name\": \"Martin\", \"identifier\": \"\", \"name\": | ||
24 | \"Sch\\u00fctz\"}, {\"affiliation\": \"WSL\", \"affiliation_02\": | 24 | \"Sch\\u00fctz\"}, {\"affiliation\": \"WSL\", \"affiliation_02\": | ||
25 | \"\", \"affiliation_03\": \"\", \"data_credit\": [\"publication\", | 25 | \"\", \"affiliation_03\": \"\", \"data_credit\": [\"publication\", | ||
26 | \"supervision\"], \"email\": \"anita.risch@wsl.ch\", \"given_name\": | 26 | \"supervision\"], \"email\": \"anita.risch@wsl.ch\", \"given_name\": | ||
27 | \"Anita C.\", \"identifier\": \"0000-0003-0531-8336\", \"name\": | 27 | \"Anita C.\", \"identifier\": \"0000-0003-0531-8336\", \"name\": | ||
28 | \"Risch\"}, {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | 28 | \"Risch\"}, {\"affiliation\": \"WSL\", \"affiliation_02\": \"\", | ||
29 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | 29 | \"affiliation_03\": \"\", \"data_credit\": [\"collection\", | ||
30 | \"publication\", \"supervision\"], \"email\": | 30 | \"publication\", \"supervision\"], \"email\": | ||
31 | \"martin.gossner@wsl.ch\", \"given_name\": \"Martin M.\", | 31 | \"martin.gossner@wsl.ch\", \"given_name\": \"Martin M.\", | ||
32 | \"identifier\": \"0000-0003-1516-6364\", \"name\": \"Gossner\"}]", | 32 | \"identifier\": \"0000-0003-1516-6364\", \"name\": \"Gossner\"}]", | ||
33 | "author_email": null, | 33 | "author_email": null, | ||
34 | "creator_user_id": "e673d4bc-4054-4784-b885-4363a52a08aa", | 34 | "creator_user_id": "e673d4bc-4054-4784-b885-4363a52a08aa", | ||
35 | "date": "[{\"date\": \"2017-07-01\", \"date_type\": \"collected\", | 35 | "date": "[{\"date\": \"2017-07-01\", \"date_type\": \"collected\", | ||
36 | \"end_date\": \"2017-07-31\"}]", | 36 | \"end_date\": \"2017-07-31\"}]", | ||
37 | "doi": "10.16904/envidat.142", | 37 | "doi": "10.16904/envidat.142", | ||
38 | "funding": "[{\"grant_number\": \"31003A_166654 / | 38 | "funding": "[{\"grant_number\": \"31003A_166654 / | ||
39 | 310030E-173542/1\", \"institution\": \"Swiss National Science | 39 | 310030E-173542/1\", \"institution\": \"Swiss National Science | ||
40 | Foundation SNF\", \"institution_url\": \"http://www.snf.ch\"}]", | 40 | Foundation SNF\", \"institution_url\": \"http://www.snf.ch\"}]", | ||
41 | "groups": [], | 41 | "groups": [], | ||
42 | "id": "e4752eb3-24f1-48b5-a6c4-e0a4134af08d", | 42 | "id": "e4752eb3-24f1-48b5-a6c4-e0a4134af08d", | ||
43 | "isopen": true, | 43 | "isopen": true, | ||
44 | "language": "en", | 44 | "language": "en", | ||
45 | "license_id": "odc-odbl", | 45 | "license_id": "odc-odbl", | ||
46 | "license_title": "ODbL with Database Contents License (DbCL)", | 46 | "license_title": "ODbL with Database Contents License (DbCL)", | ||
47 | "license_url": "https://opendefinition.org/licenses/odc-odbl", | 47 | "license_url": "https://opendefinition.org/licenses/odc-odbl", | ||
48 | "maintainer": "{\"affiliation\": \"WSL\", \"email\": | 48 | "maintainer": "{\"affiliation\": \"WSL\", \"email\": | ||
49 | \"felix.neff@wsl.ch\", \"given_name\": \"Felix\", \"identifier\": | 49 | \"felix.neff@wsl.ch\", \"given_name\": \"Felix\", \"identifier\": | ||
50 | \"0000-0001-7266-2589\", \"name\": \"Neff\"}", | 50 | \"0000-0001-7266-2589\", \"name\": \"Neff\"}", | ||
51 | "maintainer_email": null, | 51 | "maintainer_email": null, | ||
52 | "metadata_created": "2020-03-18T08:15:00.220494", | 52 | "metadata_created": "2020-03-18T08:15:00.220494", | ||
n | 53 | "metadata_modified": "2021-08-17T11:20:35.935865", | n | 53 | "metadata_modified": "2021-08-17T11:22:02.265552", |
54 | "name": "data_ecolappl_2020", | 54 | "name": "data_ecolappl_2020", | ||
55 | "notes": "This dataset contains all data, on which the following | 55 | "notes": "This dataset contains all data, on which the following | ||
56 | publication below is based.\r\n\r\n**Paper Citation**:\r\n\r\nNeff, | 56 | publication below is based.\r\n\r\n**Paper Citation**:\r\n\r\nNeff, | ||
57 | F., Resch, M. C., Marty, A., Rolley, J. D., Sch\u00fctz, M., Risch, A. | 57 | F., Resch, M. C., Marty, A., Rolley, J. D., Sch\u00fctz, M., Risch, A. | ||
58 | C, Gossner, M. M. Accepted. Long-term restoration success of insect | 58 | C, Gossner, M. M. Accepted. Long-term restoration success of insect | ||
59 | herbivore communities in semi-natural grasslands: a functional | 59 | herbivore communities in semi-natural grasslands: a functional | ||
60 | approach. Ecological Applications.\r\n\r\nPlease cite this paper | 60 | approach. Ecological Applications.\r\n\r\nPlease cite this paper | ||
61 | together with the citation for the datafile.\r\n\r\n# | 61 | together with the citation for the datafile.\r\n\r\n# | ||
62 | Methods\r\n\r\n## Study site\r\nThe study area is situated within and | 62 | Methods\r\n\r\n## Study site\r\nThe study area is situated within and | ||
63 | nearby to Eigental nature reserve (47\u00b027\u201936\u201d to | 63 | nearby to Eigental nature reserve (47\u00b027\u201936\u201d to | ||
64 | 47\u00b029\u201906\u201d N, 8\u00b037\u201912\u201d to | 64 | 47\u00b029\u201906\u201d N, 8\u00b037\u201912\u201d to | ||
65 | 8\u00b037\u201944\u201d E, 461 to 507 m a.s.l.) in the vicinity of | 65 | 8\u00b037\u201944\u201d E, 461 to 507 m a.s.l.) in the vicinity of | ||
66 | Zurich airport (Canton Zurich, Switzerland). Mean annual precipitation | 66 | Zurich airport (Canton Zurich, Switzerland). Mean annual precipitation | ||
67 | and temperature is 903 \u00b1 136 mm and 9.14\u00b0C \u00b1 | 67 | and temperature is 903 \u00b1 136 mm and 9.14\u00b0C \u00b1 | ||
68 | 0.50\u00b0C (mean \u00b1 SD for 2007-2017 (*MeteoSchweiz 2018*)). In | 68 | 0.50\u00b0C (mean \u00b1 SD for 2007-2017 (*MeteoSchweiz 2018*)). In | ||
69 | 1967, the Eigental nature reserve was established to protect small and | 69 | 1967, the Eigental nature reserve was established to protect small and | ||
70 | isolated remnants of species-rich, semi-natural grasslands (roughly 12 | 70 | isolated remnants of species-rich, semi-natural grasslands (roughly 12 | ||
71 | ha), which were embedded in an otherwise intensively managed | 71 | ha), which were embedded in an otherwise intensively managed | ||
72 | landscape. It is characterized by oligo- to mesotrophic Molinion | 72 | landscape. It is characterized by oligo- to mesotrophic Molinion | ||
73 | (semi-wet, matrix species *Molinia caerulea*) and Mesobromion | 73 | (semi-wet, matrix species *Molinia caerulea*) and Mesobromion | ||
74 | (semi-dry, matrix species *Bromus erectus*) meadows (*Delarze et al. | 74 | (semi-dry, matrix species *Bromus erectus*) meadows (*Delarze et al. | ||
75 | 2015*), reflecting small-scale habitat heterogeneity, mainly due to | 75 | 2015*), reflecting small-scale habitat heterogeneity, mainly due to | ||
76 | site-specific groundwater levels and slope inclination. As in most | 76 | site-specific groundwater levels and slope inclination. As in most | ||
77 | Central European grasslands, management is necessary to prevent shrub | 77 | Central European grasslands, management is necessary to prevent shrub | ||
78 | and tree invasions as well as to secure low levels of available soil | 78 | and tree invasions as well as to secure low levels of available soil | ||
79 | nutrients and thus to maintain these species-rich habitats ([*Poschlod | 79 | nutrients and thus to maintain these species-rich habitats ([*Poschlod | ||
80 | and WallisDeVries | 80 | and WallisDeVries | ||
81 | 2002*](https://doi.org/10.1016/S0006-3207(01)00201-4)).\r\nIn 1990, | 81 | 2002*](https://doi.org/10.1016/S0006-3207(01)00201-4)).\r\nIn 1990, | ||
82 | the government of the Canton Zurich decided to enlarge the Eigental | 82 | the government of the Canton Zurich decided to enlarge the Eigental | ||
83 | nature reserve as a counter measure against degradation and | 83 | nature reserve as a counter measure against degradation and | ||
84 | biodiversity loss in semi-natural grasslands due to overutilization | 84 | biodiversity loss in semi-natural grasslands due to overutilization | ||
85 | and the excessive input of nutrients (mostly nitrogen). Eleven patches | 85 | and the excessive input of nutrients (mostly nitrogen). Eleven patches | ||
86 | of adjacent intensively managed grassland (in total roughly 20 ha) | 86 | of adjacent intensively managed grassland (in total roughly 20 ha) | ||
87 | were targeted to be transformed into semi-natural grasslands. As a | 87 | were targeted to be transformed into semi-natural grasslands. As a | ||
88 | first restoration measure, fertilization was ceased, and biomass | 88 | first restoration measure, fertilization was ceased, and biomass | ||
89 | harvested three times to remove excessive soil nutrients from the | 89 | harvested three times to remove excessive soil nutrients from the | ||
90 | original system and thus benefit plant species with low competitive | 90 | original system and thus benefit plant species with low competitive | ||
91 | ability on the long run. In 1995, the restoration efforts were | 91 | ability on the long run. In 1995, the restoration efforts were | ||
92 | increased and a large-scale experiment comprising three restoration | 92 | increased and a large-scale experiment comprising three restoration | ||
93 | measures with increasing intervention intensities was | 93 | measures with increasing intervention intensities was | ||
94 | implemented:\r\n\r\n- **Harvest only**: Initial restoration measures | 94 | implemented:\r\n\r\n- **Harvest only**: Initial restoration measures | ||
95 | were continued with mowing and removing of the aboveground biomass two | 95 | were continued with mowing and removing of the aboveground biomass two | ||
96 | times a year (early summer and autumn).\r\n- **Topsoil**: Removal of | 96 | times a year (early summer and autumn).\r\n- **Topsoil**: Removal of | ||
97 | topsoil, depending on the thickness of the A horizon the upper 10 to | 97 | topsoil, depending on the thickness of the A horizon the upper 10 to | ||
98 | 20 cm, in four randomly selected areas within the eleven patches in | 98 | 20 cm, in four randomly selected areas within the eleven patches in | ||
99 | late autumn 1995. The size of the restoration area depended on | 99 | late autumn 1995. The size of the restoration area depended on | ||
100 | individual patch size (2700 to 7000 m2).\r\n- **Topsoil + | 100 | individual patch size (2700 to 7000 m2).\r\n- **Topsoil + | ||
101 | Propagules**: Plant propagules were added on half of the area where | 101 | Propagules**: Plant propagules were added on half of the area where | ||
102 | topsoil was removed via application of fresh, seed-containing hay and | 102 | topsoil was removed via application of fresh, seed-containing hay and | ||
103 | hand-collected propagules of target species originating from semi-dry | 103 | hand-collected propagules of target species originating from semi-dry | ||
104 | and semi-wet species-rich grasslands with local and regional | 104 | and semi-wet species-rich grasslands with local and regional | ||
105 | provenance (within radius of 7 to 30 km) (1995, 1996, | 105 | provenance (within radius of 7 to 30 km) (1995, 1996, | ||
106 | 1997).\r\n\r\nManagement of *Topsoil* and *Topsoil + Propagules* | 106 | 1997).\r\n\r\nManagement of *Topsoil* and *Topsoil + Propagules* | ||
107 | started five years after treatment implementation and included yearly | 107 | started five years after treatment implementation and included yearly | ||
108 | mowing and removing of aboveground biomass (late summer or early | 108 | mowing and removing of aboveground biomass (late summer or early | ||
109 | autumn). The experiment was complemented with intensively managed | 109 | autumn). The experiment was complemented with intensively managed | ||
110 | grassland sites that share the same agricultural history as the | 110 | grassland sites that share the same agricultural history as the | ||
111 | restored sites (**Initial**; swards dominated by *Lolium perenne*, *L. | 111 | restored sites (**Initial**; swards dominated by *Lolium perenne*, *L. | ||
112 | multiflorum* and *Trifolium repens*): mowing and subsequent | 112 | multiflorum* and *Trifolium repens*): mowing and subsequent | ||
113 | fertilizing (manure) up to five times a year, as well as different | 113 | fertilizing (manure) up to five times a year, as well as different | ||
114 | tillage regimes. Finally, sites were selected in target semi-dry and | 114 | tillage regimes. Finally, sites were selected in target semi-dry and | ||
115 | semi-wet grasslands (**Target**) located within the Eigental nature | 115 | semi-wet grasslands (**Target**) located within the Eigental nature | ||
116 | reserve and another nature reserve nearby (Altl\u00e4ufe der Glatt; | 116 | reserve and another nature reserve nearby (Altl\u00e4ufe der Glatt; | ||
117 | 47\u00b028\u201929\u201d to 47\u00b027\u201941\u201d N, | 117 | 47\u00b028\u201929\u201d to 47\u00b027\u201941\u201d N, | ||
118 | 8\u00b031\u201956\u201d to 8\u00b032\u201926\u201d E, 418 to 420 m | 118 | 8\u00b031\u201956\u201d to 8\u00b032\u201926\u201d E, 418 to 420 m | ||
119 | a.s.l.). The selected target sites are mown and aboveground biomass | 119 | a.s.l.). The selected target sites are mown and aboveground biomass | ||
120 | removed once a year in late summer or early autumn. For each of the | 120 | removed once a year in late summer or early autumn. For each of the | ||
121 | five treatments, we selected eleven plots (5 m \u00d7 5 m) spread | 121 | five treatments, we selected eleven plots (5 m \u00d7 5 m) spread | ||
122 | across the sites. Altogether, the experiment included 55 | 122 | across the sites. Altogether, the experiment included 55 | ||
123 | plots.\r\n\r\n## Arthropod sampling\r\nAboveground arthropods were | 123 | plots.\r\n\r\n## Arthropod sampling\r\nAboveground arthropods were | ||
124 | sampled using suction sampling on four consecutive days in early July | 124 | sampled using suction sampling on four consecutive days in early July | ||
125 | 2017 before the grasslands were mown. Arthropods were sampled in two | 125 | 2017 before the grasslands were mown. Arthropods were sampled in two | ||
126 | locations on each 5 m \u00d7 5 m plot, once in the south-western and | 126 | locations on each 5 m \u00d7 5 m plot, once in the south-western and | ||
127 | once in the north-eastern corner to account for possible spatial | 127 | once in the north-eastern corner to account for possible spatial | ||
128 | heterogeneity within the plots. Arthropods were sorted to order or | 128 | heterogeneity within the plots. Arthropods were sorted to order or | ||
129 | lower taxonomic levels and individuals were identified to species | 129 | lower taxonomic levels and individuals were identified to species | ||
130 | level. We focused on three groups (Hemiptera: Auchenorrhyncha, | 130 | level. We focused on three groups (Hemiptera: Auchenorrhyncha, | ||
131 | Hemiptera: Heteroptera, Orthoptera),\r\n\r\n## Functional traits\r\nWe | 131 | Hemiptera: Heteroptera, Orthoptera),\r\n\r\n## Functional traits\r\nWe | ||
132 | used two sets of functional traits in this study. | 132 | used two sets of functional traits in this study. | ||
133 | \r\n\r\n**Morphometric traits**: \r\nBody volume, body shape, hind | 133 | \r\n\r\n**Morphometric traits**: \r\nBody volume, body shape, hind | ||
134 | femur shape, hind/front leg ratio, wing length, leg length, antenna | 134 | femur shape, hind/front leg ratio, wing length, leg length, antenna | ||
135 | length and eye width. We used trait measurements from [*Simons et al. | 135 | length and eye width. We used trait measurements from [*Simons et al. | ||
136 | (2016)*](http://dx.doi.org/10.1890/15-0616.1) and [*Neff et al. | 136 | (2016)*](http://dx.doi.org/10.1890/15-0616.1) and [*Neff et al. | ||
137 | (2019)*](https://doi.org/10.1007/s10980-019-00872-1) and complemented | 137 | (2019)*](https://doi.org/10.1007/s10980-019-00872-1) and complemented | ||
138 | them with measurements on study specimens. These measurements were | 138 | them with measurements on study specimens. These measurements were | ||
139 | conducted using a high-resolution measuring stereo microscope (Leica | 139 | conducted using a high-resolution measuring stereo microscope (Leica | ||
140 | DVM6, Leica Microsystems) including automated high-resolution photo | 140 | DVM6, Leica Microsystems) including automated high-resolution photo | ||
141 | stacking with the software Leica Application Suite X (LAS X, \u00a9 | 141 | stacking with the software Leica Application Suite X (LAS X, \u00a9 | ||
142 | 2018 Leica Microsystems CMS GmbH) and Leica Map Premium (Leica | 142 | 2018 Leica Microsystems CMS GmbH) and Leica Map Premium (Leica | ||
143 | Microsystems, \u00a9 1996-2017 Digital Surf) at WSL Birmensdorf. The | 143 | Microsystems, \u00a9 1996-2017 Digital Surf) at WSL Birmensdorf. The | ||
144 | eight morphometric traits were calculated from direct measurements of | 144 | eight morphometric traits were calculated from direct measurements of | ||
145 | body parts on specimens of all sampled species. From each species, we | 145 | body parts on specimens of all sampled species. From each species, we | ||
146 | measured at least one female and one male specimen. Additionally, for | 146 | measured at least one female and one male specimen. Additionally, for | ||
147 | species that show wing dimorphism, we included the different wing | 147 | species that show wing dimorphism, we included the different wing | ||
148 | morphs and weighted them by their prevalence reported in literature. | 148 | morphs and weighted them by their prevalence reported in literature. | ||
149 | For few species, of which not all wing morphs were available for | 149 | For few species, of which not all wing morphs were available for | ||
150 | measurements (10 cases), we estimated relative wing length from | 150 | measurements (10 cases), we estimated relative wing length from | ||
151 | congeneric species or from the literature. \r\n\r\n**Life-history | 151 | congeneric species or from the literature. \r\n\r\n**Life-history | ||
152 | traits** \r\nBased on an existing data set collected by [*Gossner et | 152 | traits** \r\nBased on an existing data set collected by [*Gossner et | ||
153 | al. (2015)*](http://dx.doi.org/10.1890/14-2159.1). We included traits | 153 | al. (2015)*](http://dx.doi.org/10.1890/14-2159.1). We included traits | ||
154 | describing different life-history characteristics of herbivore insect | 154 | describing different life-history characteristics of herbivore insect | ||
155 | species, namely: feeding specialization, feeding tissue, hibernation | 155 | species, namely: feeding specialization, feeding tissue, hibernation | ||
156 | stage and number of generations per year, which are related to insect | 156 | stage and number of generations per year, which are related to insect | ||
157 | species\u2019 vulnerability to changes in plant community composition, | 157 | species\u2019 vulnerability to changes in plant community composition, | ||
158 | microhabitat use and disturbance tolerance. To represent potential | 158 | microhabitat use and disturbance tolerance. To represent potential | ||
159 | changes in habitat moisture with abandonment of intensive land use | 159 | changes in habitat moisture with abandonment of intensive land use | ||
160 | (e.g., change in ground-water level), we also included two traits | 160 | (e.g., change in ground-water level), we also included two traits | ||
161 | related to preferred habitat moisture of the study species: moisture | 161 | related to preferred habitat moisture of the study species: moisture | ||
162 | preference, describing species\u2019 optimum habitat moisture, and | 162 | preference, describing species\u2019 optimum habitat moisture, and | ||
163 | moisture range, which describes the species\u2019 range of preferable | 163 | moisture range, which describes the species\u2019 range of preferable | ||
164 | moisture conditions. \r\n\r\n\r\n### References\r\n\r\nDelarze, R., | 164 | moisture conditions. \r\n\r\n\r\n### References\r\n\r\nDelarze, R., | ||
165 | Y. Gonseth, S. Eggenberg, and M. Vust. 2015. Lebensr\u00e4ume der | 165 | Y. Gonseth, S. Eggenberg, and M. Vust. 2015. Lebensr\u00e4ume der | ||
166 | Schweiz: \u00d6kologie - Gef\u00e4hrdung - Kennarten. 3rd ed. Ott, | 166 | Schweiz: \u00d6kologie - Gef\u00e4hrdung - Kennarten. 3rd ed. Ott, | ||
167 | Bern. \r\n\r\nGossner, M. M., N. K. Simons, R. Achtziger, T. Blick, | 167 | Bern. \r\n\r\nGossner, M. M., N. K. Simons, R. Achtziger, T. Blick, | ||
168 | W. H. O. Dorow, F. Dziock, F. K\u00f6hler, W. Rabitsch, and W. W. | 168 | W. H. O. Dorow, F. Dziock, F. K\u00f6hler, W. Rabitsch, and W. W. | ||
169 | Weisser. 2015. A summary of eight traits of Coleoptera, Hemiptera, | 169 | Weisser. 2015. A summary of eight traits of Coleoptera, Hemiptera, | ||
170 | Orthoptera and Araneae, occurring in grasslands in Germany. Scientific | 170 | Orthoptera and Araneae, occurring in grasslands in Germany. Scientific | ||
171 | Data 2:150013. \r\n\r\nMeteoSchweiz. 2018. Klimabulletin Jahr 2017. | 171 | Data 2:150013. \r\n\r\nMeteoSchweiz. 2018. Klimabulletin Jahr 2017. | ||
172 | MeteoSchweiz, Z\u00fcrich. \r\n\r\nNeff, F., N. Bl\u00fcthgen, M. N. | 172 | MeteoSchweiz, Z\u00fcrich. \r\n\r\nNeff, F., N. Bl\u00fcthgen, M. N. | ||
173 | Chist\u00e9, N. K. Simons, J. Steckel, W. W. Weisser, C. Westphal, L. | 173 | Chist\u00e9, N. K. Simons, J. Steckel, W. W. Weisser, C. Westphal, L. | ||
174 | Pellissier, and M. M. Gossner. 2019. Cross-scale effects of land use | 174 | Pellissier, and M. M. Gossner. 2019. Cross-scale effects of land use | ||
175 | on the functional composition of herbivorous insect communities. | 175 | on the functional composition of herbivorous insect communities. | ||
176 | Landscape Ecology 34:2001\u20132015. \r\n\r\nPoschlod, P., and M. F. | 176 | Landscape Ecology 34:2001\u20132015. \r\n\r\nPoschlod, P., and M. F. | ||
177 | WallisDeVries. 2002. The historical and socioeconomic perspective of | 177 | WallisDeVries. 2002. The historical and socioeconomic perspective of | ||
178 | calcareous grasslands\u2014lessons from the distant and recent past. | 178 | calcareous grasslands\u2014lessons from the distant and recent past. | ||
179 | Biological Conservation 104:361\u2013376. \r\n\r\nSimons, N. K., W. | 179 | Biological Conservation 104:361\u2013376. \r\n\r\nSimons, N. K., W. | ||
180 | W. Weisser, and M. M. Gossner. 2016. Multi-taxa approach shows | 180 | W. Weisser, and M. M. Gossner. 2016. Multi-taxa approach shows | ||
181 | consistent shifts in arthropod functional traits along grassland | 181 | consistent shifts in arthropod functional traits along grassland | ||
182 | land-use intensity gradient. Ecology 97:754\u2013764. ", | 182 | land-use intensity gradient. Ecology 97:754\u2013764. ", | ||
183 | "num_resources": 3, | 183 | "num_resources": 3, | ||
184 | "num_tags": 8, | 184 | "num_tags": 8, | ||
185 | "organization": { | 185 | "organization": { | ||
186 | "approval_status": "approved", | 186 | "approval_status": "approved", | ||
187 | "created": "2019-09-12T13:05:17.879759", | 187 | "created": "2019-09-12T13:05:17.879759", | ||
188 | "description": "Our group Forest Entomology investigates forest | 188 | "description": "Our group Forest Entomology investigates forest | ||
189 | insects in their broadest sense: ecology of potential forest pests, | 189 | insects in their broadest sense: ecology of potential forest pests, | ||
190 | natural enemies, diversity of forest insects.\r\n\r\nResearch | 190 | natural enemies, diversity of forest insects.\r\n\r\nResearch | ||
191 | topics\r\n\r\n- Infestation dynamics of bark beetles, effect of | 191 | topics\r\n\r\n- Infestation dynamics of bark beetles, effect of | ||
192 | natural enemies.\r\n- Interactions between host trees and bark | 192 | natural enemies.\r\n- Interactions between host trees and bark | ||
193 | beetles\r\n- Recolonization of windthrow and wildfire areas by insect | 193 | beetles\r\n- Recolonization of windthrow and wildfire areas by insect | ||
194 | communities.\r\n- Dependency of dead wood (saproxylic) insects on tree | 194 | communities.\r\n- Dependency of dead wood (saproxylic) insects on tree | ||
195 | and stand characteristics.", | 195 | and stand characteristics.", | ||
196 | "id": "2c0895b6-f72a-4b09-bd25-9b19ed538d0f", | 196 | "id": "2c0895b6-f72a-4b09-bd25-9b19ed538d0f", | ||
197 | "image_url": "", | 197 | "image_url": "", | ||
198 | "is_organization": true, | 198 | "is_organization": true, | ||
199 | "name": "forest-entomology", | 199 | "name": "forest-entomology", | ||
200 | "state": "active", | 200 | "state": "active", | ||
201 | "title": "Forest Entomology", | 201 | "title": "Forest Entomology", | ||
202 | "type": "organization" | 202 | "type": "organization" | ||
203 | }, | 203 | }, | ||
204 | "owner_org": "2c0895b6-f72a-4b09-bd25-9b19ed538d0f", | 204 | "owner_org": "2c0895b6-f72a-4b09-bd25-9b19ed538d0f", | ||
205 | "private": false, | 205 | "private": false, | ||
206 | "publication": "{\"publication_year\": \"2020\", \"publisher\": | 206 | "publication": "{\"publication_year\": \"2020\", \"publisher\": | ||
207 | \"EnviDat\"}", | 207 | \"EnviDat\"}", | ||
208 | "publication_state": "published", | 208 | "publication_state": "published", | ||
209 | "related_datasets": "M. Carol Resch; Martin Sch\u00fctz; Anita C. | 209 | "related_datasets": "M. Carol Resch; Martin Sch\u00fctz; Anita C. | ||
210 | Risch (2019). Grassland restoration: nematodes and plant communities. | 210 | Risch (2019). Grassland restoration: nematodes and plant communities. | ||
211 | EnviDat. doi: | 211 | EnviDat. doi: | ||
212 | [10.16904/envidat.65](https://doi.org/10.16904/envidat.65).", | 212 | [10.16904/envidat.65](https://doi.org/10.16904/envidat.65).", | ||
t | 213 | "related_publications": "*wsl:23144", | t | 213 | "related_publications": "* Neff, F., Resch, M. C., Marty, A., |
214 | Rolley, J. D., Sch\u00fctz, M., Risch, A. C., & Gossner, M. M. (2020). | ||||
215 | Long\u2010term restoration success of insect herbivore communities in | ||||
216 | semi\u2010natural grasslands: a functional approach. Ecological | ||||
217 | Applications, 30(6), e02133 (12 pp.). | ||||
218 | https://www.dora.lib4ri.ch/wsl/islandora/object/wsl:23144\r\n* | ||||
219 | wsl:23144", | ||||
214 | "relationships_as_object": [], | 220 | "relationships_as_object": [], | ||
215 | "relationships_as_subject": [], | 221 | "relationships_as_subject": [], | ||
216 | "resource_type": "dataset", | 222 | "resource_type": "dataset", | ||
217 | "resource_type_general": "dataset", | 223 | "resource_type_general": "dataset", | ||
218 | "resources": [ | 224 | "resources": [ | ||
219 | { | 225 | { | ||
220 | "cache_last_updated": null, | 226 | "cache_last_updated": null, | ||
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222 | "created": "2020-03-18T08:39:32.984949", | 228 | "created": "2020-03-18T08:39:32.984949", | ||
223 | "description": "Abundance of adult insects recorded in the | 229 | "description": "Abundance of adult insects recorded in the | ||
224 | samplings on all experimental sites \r\n \r\n- **Plot**: ID of Plot | 230 | samplings on all experimental sites \r\n \r\n- **Plot**: ID of Plot | ||
225 | \r\n- **Treatment**: Experimental treatment \r\n- **Species**: | 231 | \r\n- **Treatment**: Experimental treatment \r\n- **Species**: | ||
226 | Insect species name (following [Fauna Europaea](https://fauna-eu.org)) | 232 | Insect species name (following [Fauna Europaea](https://fauna-eu.org)) | ||
227 | \r\n- **Author**: Author and year of species' description (following | 233 | \r\n- **Author**: Author and year of species' description (following | ||
228 | [Fauna Europaea](https://fauna-eu.org)) \r\n- **Group**: Insect group | 234 | [Fauna Europaea](https://fauna-eu.org)) \r\n- **Group**: Insect group | ||
229 | as used in the analyses \r\n- **Number_Adults**: Number of adult | 235 | as used in the analyses \r\n- **Number_Adults**: Number of adult | ||
230 | individuals recorded \r\n- **Herbivore**: Logical indicating whether | 236 | individuals recorded \r\n- **Herbivore**: Logical indicating whether | ||
231 | the species is feeding as a herbivore (*TRUE*) or not (*FALSE*) ", | 237 | the species is feeding as a herbivore (*TRUE*) or not (*FALSE*) ", | ||
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257 | "created": "2020-03-18T09:20:33.640695", | 263 | "created": "2020-03-18T09:20:33.640695", | ||
258 | "description": "Functional traits of all herbivorous insect | 264 | "description": "Functional traits of all herbivorous insect | ||
259 | species sampled in the study.\r\n \r\n- **Species**: Insect species | 265 | species sampled in the study.\r\n \r\n- **Species**: Insect species | ||
260 | name (following [Fauna Europaea](https://fauna-eu.org)) \r\n- | 266 | name (following [Fauna Europaea](https://fauna-eu.org)) \r\n- | ||
261 | **Author**: Author and year of species' description (following [Fauna | 267 | **Author**: Author and year of species' description (following [Fauna | ||
262 | Europaea](https://fauna-eu.org)) \r\n- **Group**: Insect group as | 268 | Europaea](https://fauna-eu.org)) \r\n- **Group**: Insect group as | ||
263 | used in the analyses \r\n- **Body volume**: Body volume determined by | 269 | used in the analyses \r\n- **Body volume**: Body volume determined by | ||
264 | body length, body width and body height (in mm$^3$) \r\n- | 270 | body length, body width and body height (in mm$^3$) \r\n- | ||
265 | **Body_shape**: Ratio of body length to body width \r\n- | 271 | **Body_shape**: Ratio of body length to body width \r\n- | ||
266 | **Hind_femur_shape**: Ratio of hind-femur length to hind-femur width | 272 | **Hind_femur_shape**: Ratio of hind-femur length to hind-femur width | ||
267 | \r\n- **Hind_front_leg_ratio**: Ratio of front-leg length to hind-leg | 273 | \r\n- **Hind_front_leg_ratio**: Ratio of front-leg length to hind-leg | ||
268 | length (leg length = femur length + tibia length) \r\n- | 274 | length (leg length = femur length + tibia length) \r\n- | ||
269 | **Wing_length_rel**: Ratio of wing length to body length \r\n- | 275 | **Wing_length_rel**: Ratio of wing length to body length \r\n- | ||
270 | **Leg_length_rel**: Ratio of front-leg length to body length (leg | 276 | **Leg_length_rel**: Ratio of front-leg length to body length (leg | ||
271 | length = femur length + tibia length) \r\n- **Antenna_length_rel**: | 277 | length = femur length + tibia length) \r\n- **Antenna_length_rel**: | ||
272 | Ratio antenna length to body length \r\n- **Eye_width_rel**: Ratio of | 278 | Ratio antenna length to body length \r\n- **Eye_width_rel**: Ratio of | ||
273 | eye width to head width (Auchenorrhyncha, Heteroptera) / to head | 279 | eye width to head width (Auchenorrhyncha, Heteroptera) / to head | ||
274 | height (Orthoptera)\r\n- **Feeding_specialization**: Insect | 280 | height (Orthoptera)\r\n- **Feeding_specialization**: Insect | ||
275 | specialization on food source (*m*: monophagous, *o*: oligophagous, | 281 | specialization on food source (*m*: monophagous, *o*: oligophagous, | ||
276 | *p*: polyphagous) \r\n- **Feeding_tissue**: Feeding tissue used for | 282 | *p*: polyphagous) \r\n- **Feeding_tissue**: Feeding tissue used for | ||
277 | feeding (*c*: chewers, *x*: xylem, *p*: phloem, *m*: mesophyll, | 283 | feeding (*c*: chewers, *x*: xylem, *p*: phloem, *m*: mesophyll, | ||
278 | *m-p/r*: mesophyll as well as phloem and/or reproductive organs, *r*: | 284 | *m-p/r*: mesophyll as well as phloem and/or reproductive organs, *r*: | ||
279 | reproductive organs, *se*: ripe seeds) \r\n- **Hibernation**: | 285 | reproductive organs, *se*: ripe seeds) \r\n- **Hibernation**: | ||
280 | Hibernation stage (*e*: egg, *e/n*: egg and nymph, *n*: nymph, *a*: | 286 | Hibernation stage (*e*: egg, *e/n*: egg and nymph, *n*: nymph, *a*: | ||
281 | adult) \r\n- **Generations**: Number of generations per year (*1.5* | 287 | adult) \r\n- **Generations**: Number of generations per year (*1.5* | ||
282 | stands for *1-2* generations per year) \r\n- **Moisture_pref_mean**: | 288 | stands for *1-2* generations per year) \r\n- **Moisture_pref_mean**: | ||
283 | mean of preferred habitat moistures (*1*: xerophilous, *2*: moderately | 289 | mean of preferred habitat moistures (*1*: xerophilous, *2*: moderately | ||
284 | xerophilous, *3*: moderately mesohygrophilous, *4*: mesohygrophilous, | 290 | xerophilous, *3*: moderately mesohygrophilous, *4*: mesohygrophilous, | ||
285 | *5*: moderately hygrophilous, *6*: hygrophilous, *7*: moderately | 291 | *5*: moderately hygrophilous, *6*: hygrophilous, *7*: moderately | ||
286 | hydrophilous, *8*: hydrophilous) \r\n- **Moisture_pref_range**: range | 292 | hydrophilous, *8*: hydrophilous) \r\n- **Moisture_pref_range**: range | ||
287 | of preferred habitat moistures (indicating degree of specialization) | 293 | of preferred habitat moistures (indicating degree of specialization) | ||
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314 | "created": "2020-03-18T09:28:23.662662", | 320 | "created": "2020-03-18T09:28:23.662662", | ||
315 | "description": "Information on the experimental plots. \r\n | 321 | "description": "Information on the experimental plots. \r\n | ||
316 | \r\n- **Plot**: ID of Plot \r\n- **Treatment**: Experimental | 322 | \r\n- **Plot**: ID of Plot \r\n- **Treatment**: Experimental | ||
317 | treatment \r\n- **Landuse_history**: recent agricultural use for | 323 | treatment \r\n- **Landuse_history**: recent agricultural use for | ||
318 | Initial; agricultural use before restoration for all restored sites | 324 | Initial; agricultural use before restoration for all restored sites | ||
319 | \r\n- **Last_tilled**: Last time the site was tilled \r\n- | 325 | \r\n- **Last_tilled**: Last time the site was tilled \r\n- | ||
320 | **Intensity**: Frequency and intensity of mowing and manuring | 326 | **Intensity**: Frequency and intensity of mowing and manuring | ||
321 | (*intensity1*: mowing once and no manure, i*ntensity2*: 2-3 times | 327 | (*intensity1*: mowing once and no manure, i*ntensity2*: 2-3 times | ||
322 | mowing and no manure, *intensity3*: 2-3 times mowing and manuring, | 328 | mowing and no manure, *intensity3*: 2-3 times mowing and manuring, | ||
323 | *intensity4*: 4-5 times mowing and manuring) \r\n- **Slope**: slope | 329 | *intensity4*: 4-5 times mowing and manuring) \r\n- **Slope**: slope | ||
324 | gradient according to classes defined by FAO (1990) \r\n- **X**: X | 330 | gradient according to classes defined by FAO (1990) \r\n- **X**: X | ||
325 | coordinate of the plot (CH1903) \r\n- **Y**: Y coordinate of the plot | 331 | coordinate of the plot (CH1903) \r\n- **Y**: Y coordinate of the plot | ||
326 | (CH1903) \r\n- **Cluster**: Spatial cluster of the plot ", | 332 | (CH1903) \r\n- **Cluster**: Spatial cluster of the plot ", | ||
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352 | "spatial_info": "Switzerland", | 358 | "spatial_info": "Switzerland", | ||
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399 | "display_name": "RESTORATION", | 405 | "display_name": "RESTORATION", | ||
400 | "id": "6d991907-cda7-4c60-9c79-ecd0056869a7", | 406 | "id": "6d991907-cda7-4c60-9c79-ecd0056869a7", | ||
401 | "name": "RESTORATION", | 407 | "name": "RESTORATION", | ||
402 | "state": "active", | 408 | "state": "active", | ||
403 | "vocabulary_id": null | 409 | "vocabulary_id": null | ||
404 | }, | 410 | }, | ||
405 | { | 411 | { | ||
406 | "display_name": "TOPSOIL REMOVAL", | 412 | "display_name": "TOPSOIL REMOVAL", | ||
407 | "id": "7096e3eb-a365-4229-9b22-e0f53fc9b10f", | 413 | "id": "7096e3eb-a365-4229-9b22-e0f53fc9b10f", | ||
408 | "name": "TOPSOIL REMOVAL", | 414 | "name": "TOPSOIL REMOVAL", | ||
409 | "state": "active", | 415 | "state": "active", | ||
410 | "vocabulary_id": null | 416 | "vocabulary_id": null | ||
411 | } | 417 | } | ||
412 | ], | 418 | ], | ||
413 | "title": "Grassland restoration: insects and insect traits", | 419 | "title": "Grassland restoration: insects and insect traits", | ||
414 | "type": "dataset", | 420 | "type": "dataset", | ||
415 | "url": null, | 421 | "url": null, | ||
416 | "version": "1.0" | 422 | "version": "1.0" | ||
417 | } | 423 | } |