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On March 16, 2021 at 5:58:28 AM UTC, Administrator:
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Changed value of field
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in Native and no-native plant interactions in Australian grasslands
f | 1 | { | f | 1 | { |
2 | "author": "[{\"affiliation\": \"Queensland University of | 2 | "author": "[{\"affiliation\": \"Queensland University of | ||
3 | Technology\", \"affiliation_02\": \"Swiss Federal Insitute for Forest, | 3 | Technology\", \"affiliation_02\": \"Swiss Federal Insitute for Forest, | ||
4 | Snow and Landscape Research WSL\", \"affiliation_03\": \"\", | 4 | Snow and Landscape Research WSL\", \"affiliation_03\": \"\", | ||
5 | \"data_credit\": [\"validation\", \"publication\", \"supervision\"], | 5 | \"data_credit\": [\"validation\", \"publication\", \"supervision\"], | ||
6 | \"email\": \"c.schlierenzauer@gmail.com\", \"given_name\": | 6 | \"email\": \"c.schlierenzauer@gmail.com\", \"given_name\": | ||
7 | \"Corinne\", \"identifier\": \"\", \"name\": \"Schlierenzauer\"}, | 7 | \"Corinne\", \"identifier\": \"\", \"name\": \"Schlierenzauer\"}, | ||
8 | {\"affiliation\": \"Swiss Federal Insitute for Forest, Snow and | 8 | {\"affiliation\": \"Swiss Federal Insitute for Forest, Snow and | ||
9 | Landscape Research WSL\", \"affiliation_02\": \"\", | 9 | Landscape Research WSL\", \"affiliation_02\": \"\", | ||
10 | \"affiliation_03\": \"\", \"data_credit\": [\"publication\", | 10 | \"affiliation_03\": \"\", \"data_credit\": [\"publication\", | ||
11 | \"supervision\"], \"email\": \"anita.risch@wsl.ch\", \"given_name\": | 11 | \"supervision\"], \"email\": \"anita.risch@wsl.ch\", \"given_name\": | ||
12 | \"Anita Christina\", \"identifier\": \"0000-0003-0531-8336\", | 12 | \"Anita Christina\", \"identifier\": \"0000-0003-0531-8336\", | ||
13 | \"name\": \"Risch\"}, {\"affiliation\": \"Swiss Federal Insitute for | 13 | \"name\": \"Risch\"}, {\"affiliation\": \"Swiss Federal Insitute for | ||
14 | Forest, Snow and Landscape Research WSL\", \"affiliation_02\": \"\", | 14 | Forest, Snow and Landscape Research WSL\", \"affiliation_02\": \"\", | ||
15 | \"affiliation_03\": \"\", \"data_credit\": [\"publication\", | 15 | \"affiliation_03\": \"\", \"data_credit\": [\"publication\", | ||
16 | \"supervision\"], \"email\": \"martin.schuetz@wsl.ch\", | 16 | \"supervision\"], \"email\": \"martin.schuetz@wsl.ch\", | ||
17 | \"given_name\": \"Martin\", \"identifier\": \"\", \"name\": | 17 | \"given_name\": \"Martin\", \"identifier\": \"\", \"name\": | ||
18 | \"Schuetz\"}, {\"affiliation\": \"Queensland University of | 18 | \"Schuetz\"}, {\"affiliation\": \"Queensland University of | ||
19 | Technology\", \"affiliation_02\": \"\", \"affiliation_03\": \"\", | 19 | Technology\", \"affiliation_02\": \"\", \"affiliation_03\": \"\", | ||
20 | \"data_credit\": [\"publication\", \"supervision\"], \"email\": | 20 | \"data_credit\": [\"publication\", \"supervision\"], \"email\": | ||
21 | \"jennifer.firn@qut.edu.au\", \"given_name\": \"Jennifer\", | 21 | \"jennifer.firn@qut.edu.au\", \"given_name\": \"Jennifer\", | ||
22 | \"identifier\": \"0000-0001-6026-8912\", \"name\": \"Firn\"}]", | 22 | \"identifier\": \"0000-0001-6026-8912\", \"name\": \"Firn\"}]", | ||
23 | "author_email": null, | 23 | "author_email": null, | ||
24 | "creator_user_id": "d30dde41-6b11-44de-9191-23cdd5bda0e9", | 24 | "creator_user_id": "d30dde41-6b11-44de-9191-23cdd5bda0e9", | ||
25 | "date": "[{\"date\": \"2020-05-01\", \"date_type\": \"collected\", | 25 | "date": "[{\"date\": \"2020-05-01\", \"date_type\": \"collected\", | ||
26 | \"end_date\": \"2021-11-30\"}]", | 26 | \"end_date\": \"2021-11-30\"}]", | ||
27 | "doi": "10.16904/envidat.214", | 27 | "doi": "10.16904/envidat.214", | ||
28 | "funding": "[{\"grant_number\": \"Discovery Grant DP190100500 \", | 28 | "funding": "[{\"grant_number\": \"Discovery Grant DP190100500 \", | ||
29 | \"institution\": \"Australian Research Council \", | 29 | \"institution\": \"Australian Research Council \", | ||
30 | \"institution_url\": \"\"}]", | 30 | \"institution_url\": \"\"}]", | ||
31 | "groups": [], | 31 | "groups": [], | ||
32 | "id": "74e353bd-5a56-419e-b8bf-0349bba7a63d", | 32 | "id": "74e353bd-5a56-419e-b8bf-0349bba7a63d", | ||
33 | "isopen": true, | 33 | "isopen": true, | ||
34 | "language": "en", | 34 | "language": "en", | ||
35 | "license_id": "odc-odbl", | 35 | "license_id": "odc-odbl", | ||
36 | "license_title": "ODbL with Database Contents License (DbCL)", | 36 | "license_title": "ODbL with Database Contents License (DbCL)", | ||
37 | "license_url": "https://opendefinition.org/licenses/odc-odbl", | 37 | "license_url": "https://opendefinition.org/licenses/odc-odbl", | ||
38 | "maintainer": "{\"affiliation\": \"\", \"email\": | 38 | "maintainer": "{\"affiliation\": \"\", \"email\": | ||
39 | \"anita.risch@wsl.ch\", \"given_name\": \"Anita C.\", \"identifier\": | 39 | \"anita.risch@wsl.ch\", \"given_name\": \"Anita C.\", \"identifier\": | ||
40 | \"\", \"name\": \"Risch\"}", | 40 | \"\", \"name\": \"Risch\"}", | ||
41 | "maintainer_email": null, | 41 | "maintainer_email": null, | ||
42 | "metadata_created": "2021-03-15T12:07:53.612726", | 42 | "metadata_created": "2021-03-15T12:07:53.612726", | ||
n | 43 | "metadata_modified": "2021-03-16T05:48:16.425769", | n | 43 | "metadata_modified": "2021-03-16T05:58:28.126325", |
44 | "name": | 44 | "name": | ||
45 | "non-native-native-plant-interactions-in-australian-grasslands", | 45 | "non-native-native-plant-interactions-in-australian-grasslands", | ||
46 | "notes": "This dataset contains all data, on which the following | 46 | "notes": "This dataset contains all data, on which the following | ||
47 | publication below is based.\r\n\r\n__Paper | 47 | publication below is based.\r\n\r\n__Paper | ||
48 | Citation:__\r\n\r\n_Schlierenzauer, C., Risch, A.C., Sch\u00fctz, M., | 48 | Citation:__\r\n\r\n_Schlierenzauer, C., Risch, A.C., Sch\u00fctz, M., | ||
49 | Firn, J. 2021. Non-native Eragrostis curvula reduces plant species | 49 | Firn, J. 2021. Non-native Eragrostis curvula reduces plant species | ||
50 | diversity in pastures of South-eastern Australia even when native | 50 | diversity in pastures of South-eastern Australia even when native | ||
51 | Themeda triandra remains co-dominant. Plants_\r\n\r\n__Please cite | 51 | Themeda triandra remains co-dominant. Plants_\r\n\r\n__Please cite | ||
52 | this paper together with the citation for the | 52 | this paper together with the citation for the | ||
53 | datafile.__\r\n\r\n\r\nStudy area\r\nThe study was conducted in the | 53 | datafile.__\r\n\r\n\r\nStudy area\r\nThe study was conducted in the | ||
54 | lowland grassy woodlands of the Bega Valley Region, which is located | 54 | lowland grassy woodlands of the Bega Valley Region, which is located | ||
55 | in the south-east corner of New South Wales, Australia. Embedded | 55 | in the south-east corner of New South Wales, Australia. Embedded | ||
56 | between the Pacific Ocean and the Australian Alps, the lowland grassy | 56 | between the Pacific Ocean and the Australian Alps, the lowland grassy | ||
57 | woodlands are mostly located on granitic substrates and reach | 57 | woodlands are mostly located on granitic substrates and reach | ||
58 | elevations of roughly 500 m above sea level. Typically, these grassy | 58 | elevations of roughly 500 m above sea level. Typically, these grassy | ||
59 | woodlands receive less precipitation (mean annual precipitation | 59 | woodlands receive less precipitation (mean annual precipitation | ||
60 | between 700-1100 mm) compared to the more elevated areas that surround | 60 | between 700-1100 mm) compared to the more elevated areas that surround | ||
61 | them (NSW Government - Office of Environment and Heritage 2017). | 61 | them (NSW Government - Office of Environment and Heritage 2017). | ||
62 | \r\nThe vegetation is dominated by an open tree canopy layer | 62 | \r\nThe vegetation is dominated by an open tree canopy layer | ||
63 | consisting of Eucalyptus tereticornis Sm, Angophora floribunda Sm. | 63 | consisting of Eucalyptus tereticornis Sm, Angophora floribunda Sm. | ||
64 | (Sweet) and a range of other eucalypt species. Sometimes shrub or | 64 | (Sweet) and a range of other eucalypt species. Sometimes shrub or | ||
65 | small trees are also present, whereas grasses and forbs form the | 65 | small trees are also present, whereas grasses and forbs form the | ||
66 | ground-cover. In areas without intensive agricultural history, this | 66 | ground-cover. In areas without intensive agricultural history, this | ||
67 | layer is dominated by perennial, tussock grasses such as Themeda | 67 | layer is dominated by perennial, tussock grasses such as Themeda | ||
68 | triandra Forssk, Microlaena stipoides R.Br (Weeping Grass), Eragrostis | 68 | triandra Forssk, Microlaena stipoides R.Br (Weeping Grass), Eragrostis | ||
69 | leptostachya Steud. (Paddock Lovegrass) and Echinopogon ovatus P.Beauv | 69 | leptostachya Steud. (Paddock Lovegrass) and Echinopogon ovatus P.Beauv | ||
70 | (Forest Hedgehog Grass). The remaining inter-tussock spaces are | 70 | (Forest Hedgehog Grass). The remaining inter-tussock spaces are | ||
71 | occupied by a diversity of growth-restricted grasses and herbaceous | 71 | occupied by a diversity of growth-restricted grasses and herbaceous | ||
72 | forbs (NSW - Department of Planing, Industries and Environment 2019; | 72 | forbs (NSW - Department of Planing, Industries and Environment 2019; | ||
73 | NSW Government - Office of Environment and Heritage 2017). | 73 | NSW Government - Office of Environment and Heritage 2017). | ||
74 | \r\nClearing, pasture sowing, fertilizer application and livestock | 74 | \r\nClearing, pasture sowing, fertilizer application and livestock | ||
75 | grazing resulted in a dramatic decrease in the extent of these natural | 75 | grazing resulted in a dramatic decrease in the extent of these natural | ||
76 | woodlands, with less than five percent within conservation reserves | 76 | woodlands, with less than five percent within conservation reserves | ||
77 | and overall, with only about 20% of their original extent in New South | 77 | and overall, with only about 20% of their original extent in New South | ||
78 | Wales still existing (Tozer et al. 2010). The remaining areas outside | 78 | Wales still existing (Tozer et al. 2010). The remaining areas outside | ||
79 | of reserves are threatened by altered fire frequencies, habitat | 79 | of reserves are threatened by altered fire frequencies, habitat | ||
80 | clearing, livestock grazing and especially by non-native plant | 80 | clearing, livestock grazing and especially by non-native plant | ||
81 | invasion, particularly Eragrostis curvula (Schrad.) Nees. For this | 81 | invasion, particularly Eragrostis curvula (Schrad.) Nees. For this | ||
82 | reason, the grassy woodlands are listed as an endangered ecological | 82 | reason, the grassy woodlands are listed as an endangered ecological | ||
83 | community in the NSW state legislation. Additionally, they are | 83 | community in the NSW state legislation. Additionally, they are | ||
84 | considered as critically endangered by the Commonwealth of Australia | 84 | considered as critically endangered by the Commonwealth of Australia | ||
85 | (Threatened Species Scientific Committee (TSSC) | 85 | (Threatened Species Scientific Committee (TSSC) | ||
86 | 2013).\r\n\r\nExperimental design and sampling\r\nThe study was | 86 | 2013).\r\n\r\nExperimental design and sampling\r\nThe study was | ||
87 | conducted on six farms and in each of them two sites were chosen, | 87 | conducted on six farms and in each of them two sites were chosen, | ||
88 | representing a paired design. One of the sites at each farm is | 88 | representing a paired design. One of the sites at each farm is | ||
89 | dominated by native Themeda triandra, the other one co-dominated by | 89 | dominated by native Themeda triandra, the other one co-dominated by | ||
90 | non-native Eragrostis curvula and Themeda triandra. All farms are | 90 | non-native Eragrostis curvula and Themeda triandra. All farms are | ||
91 | within a radius of approximately 10 km from the town Candelo. Three of | 91 | within a radius of approximately 10 km from the town Candelo. Three of | ||
92 | the farms are located North (36\u00b040\u2019 to 36\u00b042\u2019 S | 92 | the farms are located North (36\u00b040\u2019 to 36\u00b042\u2019 S | ||
93 | and 149\u00b038\u2019 to 149\u00b042\u2019 E) and three of them are | 93 | and 149\u00b038\u2019 to 149\u00b042\u2019 E) and three of them are | ||
94 | located South (36\u00b051\u2019 to 36\u00b049\u2019 S and | 94 | located South (36\u00b051\u2019 to 36\u00b049\u2019 S and | ||
95 | 149\u00b038\u2019 to 149\u00b042\u2019 E) of Candelo. \r\nNon-native | 95 | 149\u00b038\u2019 to 149\u00b042\u2019 E) of Candelo. \r\nNon-native | ||
96 | herbivores (mainly cattle, sheep and rabbits) and native herbivorous | 96 | herbivores (mainly cattle, sheep and rabbits) and native herbivorous | ||
97 | marsupials (mainly kangaroos, wallabies and wombats) are present in | 97 | marsupials (mainly kangaroos, wallabies and wombats) are present in | ||
98 | the area of these sites. On each site, data was collected within four | 98 | the area of these sites. On each site, data was collected within four | ||
99 | plots (each 1 x 1 m) in May and November 2020. All plant species found | 99 | plots (each 1 x 1 m) in May and November 2020. All plant species found | ||
100 | within a plot were recorded and their relative abundance was | 100 | within a plot were recorded and their relative abundance was | ||
101 | estimated.\r\n\r\nReferences\r\nNSW - Department of Planing, | 101 | estimated.\r\n\r\nReferences\r\nNSW - Department of Planing, | ||
102 | Industries and Environment. 2019. \u201cLowland Grassy Woodland in the | 102 | Industries and Environment. 2019. \u201cLowland Grassy Woodland in the | ||
103 | South East Corner Bioregion - Endangered Ecological Community | 103 | South East Corner Bioregion - Endangered Ecological Community | ||
104 | Listing.\u201d | 104 | Listing.\u201d | ||
105 | woodland-south-east-corner-bioregion-endangered-ecological-community-l | 105 | woodland-south-east-corner-bioregion-endangered-ecological-community-l | ||
106 | (February 18, 2021).\r\nNSW Government - Office of Environment and | 106 | (February 18, 2021).\r\nNSW Government - Office of Environment and | ||
107 | Heritage. 2017. \u201cLowland Grassy Woodland in the South East Corner | 107 | Heritage. 2017. \u201cLowland Grassy Woodland in the South East Corner | ||
108 | Bioregion - Profile.\u201d | 108 | Bioregion - Profile.\u201d | ||
109 | /www.environment.nsw.gov.au/threatenedSpeciesApp/profile.aspx?id=20070 | 109 | /www.environment.nsw.gov.au/threatenedSpeciesApp/profile.aspx?id=20070 | ||
110 | (January 31, 2021).\r\nThreatened Species Scientific Committee (TSSC). | 110 | (January 31, 2021).\r\nThreatened Species Scientific Committee (TSSC). | ||
111 | 2013. Environment Protection and Biodiversity Conservation Act 1999 | 111 | 2013. Environment Protection and Biodiversity Conservation Act 1999 | ||
112 | (EPBC Act) Conservation Advice for Lowland Grassy Woodland in the | 112 | (EPBC Act) Conservation Advice for Lowland Grassy Woodland in the | ||
113 | South East Corner Bioregion. | 113 | South East Corner Bioregion. | ||
114 | sity/threatened/communities/pubs/82-conservation-advice.pdf.\r\nTozer, | 114 | sity/threatened/communities/pubs/82-conservation-advice.pdf.\r\nTozer, | ||
115 | Mark et al. 2010. \u201cNative Vegetation of Southeast NSW: A Revised | 115 | Mark et al. 2010. \u201cNative Vegetation of Southeast NSW: A Revised | ||
116 | Classification and Map for the Coast and Eastern Tablelands.\u201d | 116 | Classification and Map for the Coast and Eastern Tablelands.\u201d | ||
117 | Cunninghamia\u202f: a journal of plant ecology for eastern Australia | 117 | Cunninghamia\u202f: a journal of plant ecology for eastern Australia | ||
118 | 11(3): 359\u2013406.\r\n\r\n", | 118 | 11(3): 359\u2013406.\r\n\r\n", | ||
119 | "num_resources": 1, | 119 | "num_resources": 1, | ||
120 | "num_tags": 5, | 120 | "num_tags": 5, | ||
121 | "organization": { | 121 | "organization": { | ||
122 | "approval_status": "approved", | 122 | "approval_status": "approved", | ||
123 | "created": "2018-04-20T09:51:26.756810", | 123 | "created": "2018-04-20T09:51:26.756810", | ||
124 | "description": "We are studying the distribution of and | 124 | "description": "We are studying the distribution of and | ||
125 | interactions among producers, consumers as well as decomposers and | 125 | interactions among producers, consumers as well as decomposers and | ||
126 | between these communities and their environment. We focus on food webs | 126 | between these communities and their environment. We focus on food webs | ||
127 | in real world ecosystems and thus mainly sample our data during | 127 | in real world ecosystems and thus mainly sample our data during | ||
128 | experimental field campaigns. Data collection under controlled | 128 | experimental field campaigns. Data collection under controlled | ||
129 | conditions in the greenhouse or experimental garden are, however, | 129 | conditions in the greenhouse or experimental garden are, however, | ||
130 | common add-ons hereby. We are mainly interested in the functioning of | 130 | common add-ons hereby. We are mainly interested in the functioning of | ||
131 | natural ecosystems and often conduct research in National Parks around | 131 | natural ecosystems and often conduct research in National Parks around | ||
132 | the world. Our main study area is, however, the Swiss National Park. | 132 | the world. Our main study area is, however, the Swiss National Park. | ||
133 | While working on basic research questions, we regularly consider | 133 | While working on basic research questions, we regularly consider | ||
134 | applied aspects that are related to protecting or conserving | 134 | applied aspects that are related to protecting or conserving | ||
135 | endangered ecosystems.\r\n\r\nExamples of research question of our | 135 | endangered ecosystems.\r\n\r\nExamples of research question of our | ||
136 | research group assesses are:\r\n\r\nHow is species loss related to | 136 | research group assesses are:\r\n\r\nHow is species loss related to | ||
137 | ecosystem processes and functions? Which species or species groups are | 137 | ecosystem processes and functions? Which species or species groups are | ||
138 | particularly relevant for ecosystem functioning? Which effects are | 138 | particularly relevant for ecosystem functioning? Which effects are | ||
139 | expected with the loss of such important species groups? How are | 139 | expected with the loss of such important species groups? How are | ||
140 | aboveground organisms interacting with belowground organisms? Which | 140 | aboveground organisms interacting with belowground organisms? Which | ||
141 | abiotic and biotic conditions favor diverse ecosystems? Is global | 141 | abiotic and biotic conditions favor diverse ecosystems? Is global | ||
142 | change (for example eutrophication, habitat fragmentation, climate) a | 142 | change (for example eutrophication, habitat fragmentation, climate) a | ||
143 | thread for diverse ecosystems? How can diverse ecosystems be | 143 | thread for diverse ecosystems? How can diverse ecosystems be | ||
144 | protected?", | 144 | protected?", | ||
145 | "id": "60e92a46-5f9b-4a06-a32e-6a5e04869486", | 145 | "id": "60e92a46-5f9b-4a06-a32e-6a5e04869486", | ||
146 | "image_url": "2018-07-10-090227.680797LogoWSL.svg", | 146 | "image_url": "2018-07-10-090227.680797LogoWSL.svg", | ||
147 | "is_organization": true, | 147 | "is_organization": true, | ||
148 | "name": "plant-animal-interactions", | 148 | "name": "plant-animal-interactions", | ||
149 | "state": "active", | 149 | "state": "active", | ||
150 | "title": "Plant-Animal Interactions", | 150 | "title": "Plant-Animal Interactions", | ||
151 | "type": "organization" | 151 | "type": "organization" | ||
152 | }, | 152 | }, | ||
153 | "owner_org": "60e92a46-5f9b-4a06-a32e-6a5e04869486", | 153 | "owner_org": "60e92a46-5f9b-4a06-a32e-6a5e04869486", | ||
154 | "private": false, | 154 | "private": false, | ||
155 | "publication": "{\"publication_year\": \"2021\", \"publisher\": | 155 | "publication": "{\"publication_year\": \"2021\", \"publisher\": | ||
156 | \"EnviDat\"}", | 156 | \"EnviDat\"}", | ||
t | 157 | "publication_state": "pub_pending", | t | 157 | "publication_state": "approved", |
158 | "related_datasets": "", | 158 | "related_datasets": "", | ||
159 | "related_publications": "", | 159 | "related_publications": "", | ||
160 | "relationships_as_object": [], | 160 | "relationships_as_object": [], | ||
161 | "relationships_as_subject": [], | 161 | "relationships_as_subject": [], | ||
162 | "resource_type": "dataset", | 162 | "resource_type": "dataset", | ||
163 | "resource_type_general": "dataset", | 163 | "resource_type_general": "dataset", | ||
164 | "resources": [ | 164 | "resources": [ | ||
165 | { | 165 | { | ||
166 | "cache_last_updated": null, | 166 | "cache_last_updated": null, | ||
167 | "cache_url": null, | 167 | "cache_url": null, | ||
168 | "created": "2021-03-15T12:12:27.799642", | 168 | "created": "2021-03-15T12:12:27.799642", | ||
169 | "description": "__taxa tab:\tlist and overview of all the | 169 | "description": "__taxa tab:\tlist and overview of all the | ||
170 | recorded species__\r\n\r\n* family: | 170 | recorded species__\r\n\r\n* family: | ||
171 | family of the plant \r\n\r\n* genus: | 171 | family of the plant \r\n\r\n* genus: | ||
172 | genus of the plant \r\n\r\n* species: | 172 | genus of the plant \r\n\r\n* species: | ||
173 | plant species name\r\n\r\n* origin: | 173 | plant species name\r\n\r\n* origin: | ||
174 | indicates whether the plant is native to Australia or not | 174 | indicates whether the plant is native to Australia or not | ||
175 | (non-native)\r\n\r\n* common name:\t common name of the | 175 | (non-native)\r\n\r\n* common name:\t common name of the | ||
176 | plant species\r\n\r\n* functional group:\t functional | 176 | plant species\r\n\r\n* functional group:\t functional | ||
177 | group of the plant species: forb, graminoid, fern, tree\r\n\r\n* | 177 | group of the plant species: forb, graminoid, fern, tree\r\n\r\n* | ||
178 | functional group detailed:\tgives more detail about the type of | 178 | functional group detailed:\tgives more detail about the type of | ||
179 | graminoid and forb: legume, forb (non-leguminous), \r\n | 179 | graminoid and forb: legume, forb (non-leguminous), \r\n | ||
180 | grass, sedge, rush, fern, tree\r\n\r\n* lifeform: | 180 | grass, sedge, rush, fern, tree\r\n\r\n* lifeform: | ||
181 | annual or perennial lifeform (species which can have both of these | 181 | annual or perennial lifeform (species which can have both of these | ||
182 | lifeforms where\r\n | 182 | lifeforms where\r\n | ||
183 | considered as annuals)\r\n\r\n\r\n__plot tab:\tlist of species found | 183 | considered as annuals)\r\n\r\n\r\n__plot tab:\tlist of species found | ||
184 | in each plot and their cover (%)__\r\n\r\n* sampling.session: | 184 | in each plot and their cover (%)__\r\n\r\n* sampling.session: | ||
185 | provides information about the sampling time: \r\n | 185 | provides information about the sampling time: \r\n | ||
186 | May2020 = data that was collected in May 2020\r\n | 186 | May2020 = data that was collected in May 2020\r\n | ||
187 | Nov2020 = data that was collected in November 2020\r\n\r\n* | 187 | Nov2020 = data that was collected in November 2020\r\n\r\n* | ||
188 | farm.name:\t name of the farms where the | 188 | farm.name:\t name of the farms where the | ||
189 | sampling took place: \r\n | 189 | sampling took place: \r\n | ||
190 | SF = farm of the Southern group\r\n | 190 | SF = farm of the Southern group\r\n | ||
191 | NF = farm of the Northern group\r\n | 191 | NF = farm of the Northern group\r\n | ||
192 | numbers 1-3 = randomly allocated to the Southern group of farms\r\n | 192 | numbers 1-3 = randomly allocated to the Southern group of farms\r\n | ||
193 | numbers 4-6 = randomly allocated to the Northern group of | 193 | numbers 4-6 = randomly allocated to the Northern group of | ||
194 | farms\r\n\r\n* site.type:\t KG: | 194 | farms\r\n\r\n* site.type:\t KG: | ||
195 | Kangaroo grass dominated site\r\n | 195 | Kangaroo grass dominated site\r\n | ||
196 | ALG: ALG+KG site (Kangarooo grass and African lovegrass co-dominated | 196 | ALG: ALG+KG site (Kangarooo grass and African lovegrass co-dominated | ||
197 | site)\r\n\r\n* plot.no: plot number: | 197 | site)\r\n\r\n* plot.no: plot number: | ||
198 | 9-12 \r\n\r\n* scientific.name:\t scientific name of | 198 | 9-12 \r\n\r\n* scientific.name:\t scientific name of | ||
199 | the plant species found in a certain plot\r\n\r\n* functional group:\t | 199 | the plant species found in a certain plot\r\n\r\n* functional group:\t | ||
200 | indicates whether the species found is a tree, forb, graminoid or | 200 | indicates whether the species found is a tree, forb, graminoid or | ||
201 | fern\r\n\r\n* functional group detailed:\tindicates whether the | 201 | fern\r\n\r\n* functional group detailed:\tindicates whether the | ||
202 | species found is a tree, legume, forb (non-leguminous), \r\n | 202 | species found is a tree, legume, forb (non-leguminous), \r\n | ||
203 | grass, sedge, rush, fern\r\n\r\n* lifeform: | 203 | grass, sedge, rush, fern\r\n\r\n* lifeform: | ||
204 | specifies the lifeform of the species: annual or perennial lifeform | 204 | specifies the lifeform of the species: annual or perennial lifeform | ||
205 | \r\n (species which can | 205 | \r\n (species which can | ||
206 | have both of these lifeforms where considered as annuals)", | 206 | have both of these lifeforms where considered as annuals)", | ||
207 | "doi": "", | 207 | "doi": "", | ||
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214 | "mimetype_inner": null, | 214 | "mimetype_inner": null, | ||
215 | "name": "Data file native and no-native plant interactions in | 215 | "name": "Data file native and no-native plant interactions in | ||
216 | Australian grasslands", | 216 | Australian grasslands", | ||
217 | "package_id": "74e353bd-5a56-419e-b8bf-0349bba7a63d", | 217 | "package_id": "74e353bd-5a56-419e-b8bf-0349bba7a63d", | ||
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225 | "state": "active", | 225 | "state": "active", | ||
226 | "url": | 226 | "url": | ||
227 | 24e-0f9f-4d2a-ba39-93d20f6e459a/download/data_plots_2020_plants.xlsx", | 227 | 24e-0f9f-4d2a-ba39-93d20f6e459a/download/data_plots_2020_plants.xlsx", | ||
228 | "url_type": "upload" | 228 | "url_type": "upload" | ||
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231 | "spatial": | 231 | "spatial": | ||
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233 | "spatial_info": "Australia", | 233 | "spatial_info": "Australia", | ||
234 | "state": "active", | 234 | "state": "active", | ||
235 | "subtitle": "", | 235 | "subtitle": "", | ||
236 | "tags": [ | 236 | "tags": [ | ||
237 | { | 237 | { | ||
238 | "display_name": "GRASSLAND", | 238 | "display_name": "GRASSLAND", | ||
239 | "id": "fa420fc0-5693-4358-bc61-4951b239457c", | 239 | "id": "fa420fc0-5693-4358-bc61-4951b239457c", | ||
240 | "name": "GRASSLAND", | 240 | "name": "GRASSLAND", | ||
241 | "state": "active", | 241 | "state": "active", | ||
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244 | { | 244 | { | ||
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251 | { | 251 | { | ||
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253 | "id": "25583b57-2ec5-459a-b4ef-5d32073d7373", | 253 | "id": "25583b57-2ec5-459a-b4ef-5d32073d7373", | ||
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256 | "vocabulary_id": null | 256 | "vocabulary_id": null | ||
257 | }, | 257 | }, | ||
258 | { | 258 | { | ||
259 | "display_name": "NON-NATIVE PLANT", | 259 | "display_name": "NON-NATIVE PLANT", | ||
260 | "id": "d39b6831-c7c3-4c71-8028-d9b71c6cec0b", | 260 | "id": "d39b6831-c7c3-4c71-8028-d9b71c6cec0b", | ||
261 | "name": "NON-NATIVE PLANT", | 261 | "name": "NON-NATIVE PLANT", | ||
262 | "state": "active", | 262 | "state": "active", | ||
263 | "vocabulary_id": null | 263 | "vocabulary_id": null | ||
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265 | { | 265 | { | ||
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267 | "id": "0a7a70f9-d7ba-4b29-85be-5a0cd5cf60a3", | 267 | "id": "0a7a70f9-d7ba-4b29-85be-5a0cd5cf60a3", | ||
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270 | "vocabulary_id": null | 270 | "vocabulary_id": null | ||
271 | } | 271 | } | ||
272 | ], | 272 | ], | ||
273 | "title": "Native and no-native plant interactions in Australian | 273 | "title": "Native and no-native plant interactions in Australian | ||
274 | grasslands", | 274 | grasslands", | ||
275 | "type": "dataset", | 275 | "type": "dataset", | ||
276 | "url": null, | 276 | "url": null, | ||
277 | "version": "1.0" | 277 | "version": "1.0" | ||
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