High priority taxa
Following taxa (27 out of 31) were found to be high priority taxa to collect:
- S. amplum
- S. angustum
- S. aterrimum
- S. brachypodum
- S. bulbosum
- S. ecarinatum
- S. exstans
- S. grande
- S. halepense
- S. interjectum
- S. intrans
- S. laxiflorum
- S. leiocladum
- S. macrospermum
- S. matarankense
- S. miliaceum
- S. mjoebergii
- S. nitidum
- S. pauciflorum
- S. plumosum
- S. propinquum
- S. somaliense
- S. stipoideum
- S. timorense
- S. trichocladum
- S. usorum
- S. versicolor
See the priorities list here
Identified gaps for Sorghum genepool
(see downloads)
We found data for 29 wild species and 2 infraspecific taxa (S. bicolor subsp. drummondii, S. bicolor subsp. arundinaceum), accounting to a total of 31 taxa for analysis. We have classified Sorghum taxa using Stenhouse et al., (1997) genepool classification, which suggest the following genepools:
|
Primary genepool
|
Secondary genepool
|
Tertiary genepool
|
|
S. bicolor subsp. bicolor cultivars and races
|
S. halepense
|
All other sections/subgenera of Sorghum
|
|
S. bicolor subsp. arundinaceum
|
|
|
|
S. bicolor subsp. drummondii
|
||
|
S. propinquum
|
The analysis dataset (download) contained 4,337 observations, with 4,111 (95%) being herbarium specimens and 226 (5%) being genebank accessions. The average number of total samples per taxon was 140 (standard deviation of 426), indicating that available data is relatively abundant, although it is concentrated in certain taxa (i.e. S. halepense [2,399], S. plumosum [276], S. stipoideum [226], S. bicolor subsp. arundinaceum [146], S. bicolor subsp. drummondii [147]). Other taxa such as S. pauciflorum (1), S. usorum (1) and S. somaliense (2), along with others, present a very limited sampling and/or data availability and thus need further characterization and sampling for assessing a reliable ecogeographic evaluation on them.
The gap analysis of the Sorghum genepool showed that there are 27 taxa that are either underrepresented or not represented in any way in genebanks out of the 31 taxa under analysis and these taxa were therefore flagged as high priority species. 7 of these taxa presented only 10 or less data points (sum of herbarium and germplasm), which indicate that these species in particular need to be further collected (i.e. S. pauciflorum, S. usorum, S. aterrimum, S. miliaceum, S. somaliense, S. mjoebergii, S. trichocladum). There were no species flagged as very well conserved ex-situ, which indicates either genebanks are or correctly storing wild Sorghum diversity or access to their data is not available. Species S. almum and S. purpureo-sericeum appear to be relatively poorly conserved and were thus flagged as medium priority species, whilst taxa S. bicolor subsp. arundinaceum and S. bicolor subsp. drummondii appear to be the most conserved taxa among the genepool.
Potential sampling zones
Sorghum high priority taxa were found to be distributed in central Asia, part of Oceania, India and Africa. Zones in the figures above are those in which the species is likely to exist and no genebank accessions have been collected.
Potential sampling richness
The greatest sampling-richness was found in the Northern Territory of Australia.
Brief description of data used in the analysis
The table below shows the number of records (herbarium, germplasm, total) used per species for the Eleusine genepool gap analysis.
|
Species
|
Genebank accessions
|
Herbarium samples
|
Total
|
| Sorghum amplum |
0
|
18
|
18
|
| Sorghum angustum |
0
|
23
|
23
|
| Sorghum aterrimum |
0
|
2
|
2
|
| Sorghum brachypodum |
0
|
27
|
27
|
| Sorghum bulbosum |
0
|
48
|
48
|
| Sorghum ecarinatum |
0
|
11
|
11
|
| Sorghum exstans |
0
|
42
|
42
|
| Sorghum grande |
0
|
17
|
17
|
| Sorghum halepense |
6
|
2393
|
2399
|
| Sorghum interjectum |
0
|
45
|
45
|
| Sorghum intrans |
1
|
109
|
110
|
| Sorghum laxiflorum |
0
|
100
|
100
|
| Sorghum leiocladum |
0
|
177
|
177
|
| Sorghum macrospermum |
0
|
19
|
19
|
| Sorghum matarankense |
0
|
22
|
22
|
| Sorghum miliaceum |
0
|
2
|
2
|
| Sorghum mjoebergii |
0
|
4
|
4
|
| Sorghum nitidum |
0
|
164
|
164
|
| Sorghum pauciflorum |
0
|
1
|
1
|
| Sorghum plumosum |
1
|
275
|
276
|
| Sorghum propinquum |
0
|
24
|
24
|
| Sorghum somaliense |
0
|
2
|
2
|
| Sorghum stipoideum |
0
|
226
|
226
|
| Sorghum timorense |
0
|
173
|
173
|
| Sorghum trichocladum |
0
|
7
|
7
|
| Sorghum usorum |
0
|
1
|
1
|
| Sorghum versicolor |
6
|
6
|
12
|
| Sorghum bicolor subsp. arundinaceum |
75
|
71
|
146
|
| Sorghum bicolor subsp. drummondii |
113
|
34
|
147
|
| Sorghum almum |
16
|
63
|
79
|
| Sorghum purpureosericeum |
8
|
5
|
13
|
Species’ taxonomy was reviewed using Maxted and Kell (2009) as a first stage, the GRIN taxonomical review in second place, and the Royal Botanic Gardens, Kew taxonomy database. After cross-checking and correcting both synonyms and orthography of the species’ names, a thorough georeferencing process is carried out to obtain a spatially explicit database containing as many records as possible for each species. After this, records outside continental boundaries were deleted and a final dataset was produced for analyses.
These are the 61 different collections from which data were readily available:
- Árboles de la Península de Yucatán, Flora del Distrito de Tehuantepec, Oaxaca y Familia Asteraceae en México (IBUNAM)
- Arizona State University Vascular Plant Herbarium
- Australian National Herbarium (CANB)
- BDBCV BioBlitz in Penyagolosa (Castellon, Spain)
- Biodiversidad de Costa Rica
- Bishop Museum Natural History Specimen Data
- Botanical Society of the British Isles - Vascular Plants Database
- Bundesamt fuer Naturschutz / Netzwerk Phytodiversitaet Deutschland
- California State University, Chico
- Database Schema for UC Davis [Herbarium Labels]
- Direccion General de Investigacion, Desarrollo Tecnologico e Innovacion de la Junta de Extremadura(DGIDTI): HSS
- EURISCO, The European Genetic Resources Search Catalogue
- Fairchild Tropical Botanic Garden Virtual Herbarium Darwin Core format
- FloVegSI - Floristical and fitocenological database of ZRC SAZU
- Galapagos grasses and sedges
- Herbario de la Universidad de Sevilla, SEV-Historico
- Herbario del Instituto de Ecologia, A.C., México (IE-BAJIO)
- Herbarium (UNA)
- Herbarium GJO
- Herbarium of Oskarshamn (OHN)
- Herbarium Specimens of Bonin and Ryukyu Islands
- Herbarium Specimens of Museum of Nature and Human Activities, Hyogo Pref., Japan
- Herbarium Willing
- Herbarium WU
- Herbier de la Guyane
- Hortus Botanicus Sollerensis Herbarium (FBonaf+¿)
- ICRISAT SORGHUM
- Instituto de Ciencias Naturales
- IPK Genebank
- Israel Nature and Parks Authority
- Leiner-Herbar Konstanz
- Lund Botanical Museum (LD)
- MEXU/Plantas Vasculares
- Missouri Botanical Garden
- Natural History Museum Rotterdam (NMR)
- New Zealand National Plant Herbarium (CHR)
- Nordic Herbarium (S)
- NSW herbarium collection
- Observations du Conservatoire botanique national du Bassin parisien.
- Phanerogamie
- Plants (GBIF-SE:Artdatabanken)
- Plants of Papua New Guinea
- Real Jardin Botanico (Madrid), Vascular Plant Herbarium (MA)
- Repatriacion de datos del Herbario de Arizona (ARIZ)
- Specimen Database of Colorado Vascular Plants
- The AAU Herbarium Database
- The Deaver Herbarium, Northern Arizona University
- The System-wide Information Network for Genetic Resources (SINGER)
- United States National Plant Germplasm System Collection
- Universidad de Almeria, HUAL
- Universidad de Extremadura, UNEX
- Universidad de Malaga: MGC-Cormof
- University and Jepson Herbaria DiGIR provider
- USDA PLANTS Database
- USU-UTC Specimen Database
- Utah Valley State College Herbarium
- Vascular Plant Collection
- Vascular Plant Collection - University of Washington Herbarium (WTU)
- Vascular Plant Herbarium, Oslo (O)
- Vascular Plant Type Specimens
- Zoological specimens
Downloads
| Climatic niche model for S. almum | |
| Climatic niche model for S. amplum | |
| Climatic niche model for S. angustum | |
| Climatic niche model for S. bicolor subsp.arundinaceum | |
| Climatic niche model for S. bicolor subsp. drummondii | |
| Climatic niche model for S. brachypodum | |
| Climatic niche model for S. bulbosum | |
| Climatic niche model for S. ecarinatum | |
| Climatic niche model for S. exstans | |
| Climatic niche model for S. grande | |
| Climatic niche model for S. halepense | |
| Climatic niche model for S. interjectum | |
| Climatic niche model for S. intrans | |
| Climatic niche model for S. leiocladum | |
| Climatic niche model for S. matarankense | |
| Climatic niche model for S. nitidum | |
| Climatic niche model for S. plumosum | |
| Climatic niche model for S. propinquum | |
| Climatic niche model for S. purpureosericeum | |
| Climatic niche model for S. stipoideum | |
| Climatic niche model for S. timorense | |
| Sorghum potential collecting zones | |
| Sorghum potential collecting richness | |
| Predicted species richness under current climatic conditions | |
| Predicted species richness under future climatic conditions | |
| Changes on predicted species richness due to climate change | |
| Sampling density (200km cell size) for germplasm accessions | |
| Sampling density (200km cell size) for herbarium samples | |
| Conservation priorities list for Sorghum genepool | |
| Dataset used for this analysis |





