High priority taxa
Following taxa (47 out of 55) were found to be high priority taxa to collect:
- P. alopecuroides
- P. annuum
- P. bambusiforme
- P. basedowii
- P. chilense
- P. clandestinum
- P. complanatum
- P. crinitum
- P. domingense
- P. durum
- P. frutescens
- P. hohenackeri
- P. hordeoides
- P. intectum
- P. karwinskyi
- P. lanatum
- P. latifolium
- P. longissimum
- P. longistylum
- P. macrostachyum
- P. macrourum
- P. monostigma
- P. montanum
- P. nervosum
- P. occidentale
- P. pauperum
- P. pennisetiforme
- P. peruvianum
- P. polystachion
- P. polystachion subsp. atrichum
- P. polystachion subsp. polystachion
- P. prolificum
- P. purpureum
- P. riparium
- P. sagittatum
- P. schweinfurthii
- P. setaceum
- P. setigerum
- P. sieberianum
- P. squamulatum
- P. tempisquense
- P. thunbergii
- P. trachyphyllum
- P. tristachyum
- P. unisetum
- P. villosum
- P. weberbaueri
See the priorities list here
Identified gaps for Pennisetum genepool
(see downloads)
We found data for 53 wild species and 2 infraspecific taxa, accounting to a total of 55 taxa. These different taxa are classified as follows, according to their closeness to the cropped species P. glaucum using Maxted and Kell (2009) as follows:
|
Primary wild relatives
|
Secondary wild relatives
|
Tertiary wild relatives
|
|
P. glaucum cultivars and landraces
|
P. purpureum
|
All other species in the genus
|
|
P. glaucum subsp. monodii
|
P. squamulatum
|
|
|
P. glaucum subsp. stenostachyum
|
|
The analysis dataset (download) contained 4,326 observations, with 3,364 (78%) being herbarium specimens and 962 (74%) being genebank accessions. The average number of total samples per taxon was 79 (standard deviation of 163), indicating that available data is not particularly limited, although it is concentrated in certain taxa (i.e. P. ciliare, P. polystachion, P. purpureum, P. violaceum, P. clandestinum, P. villosum). Other taxa such as P. domingense (1), and P. lanatum (1) and P. sieberianum 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 Pennisetum genepool showed that there are 47 taxa that are either underrepresented or not represented in any way in genebanks out of the 55 taxa under analysis and these taxa was therefore flagged as high priority species. 26 of these taxa presented only 10 data points (sum of herbarium and germplasm), which indicates that these species in particular need to be further collected. Only species P. violaceum was found to be adequately represented in genebanks, while P. ciliare, P. flaccidum, P. orientale and P. pedicellatum were found to be relatively underrepresented and thus flagged as medium priority species, and P. divisum, P. mezianum and P. sphacelatum were found to be relatively well represented ex-situ.
Potential sampling zones
Pennisetum high priority taxa were found to be distributed in Central and South America, Africa, the Arabic Peninsula, Australia and southeastern Asia. Zones in the map above are those in which the species is likely to exist and no genebank accessions have been collected
Potential sampling richness
Several great sampling-richness were found (i.e. Andean region in South America, subsaharian Africa, Argentina’s northeastern region).
Brief description of data used in the analysis
P. glaucum was originated in western Africa, its closest wild relatives are found in arid regions of west and east Africa (Maxted and Kell, 2009). Following table shows the number of records (herbarium, germplasm, total) used per species for the Hordeum genepool gap analysis.
|
Species
|
Genebank accessions
|
Herbarium samples
|
Total
|
| Pennisetum alopecuroides |
0
|
197
|
197
|
| Pennisetum annuum |
0
|
2
|
2
|
| Pennisetum bambusiforme |
0
|
124
|
124
|
| Pennisetum basedowii |
0
|
41
|
41
|
| Pennisetum chilense |
0
|
26
|
26
|
| Pennisetum clandestinum |
2
|
283
|
285
|
| Pennisetum complanatum |
0
|
31
|
31
|
| Pennisetum crinitum |
0
|
24
|
24
|
| Pennisetum domingense |
0
|
1
|
1
|
| Pennisetum durum |
0
|
7
|
7
|
| Pennisetum frutescens |
0
|
3
|
3
|
| Pennisetum hohenackeri |
2
|
0
|
2
|
| Pennisetum hordeoides |
0
|
13
|
13
|
| Pennisetum intectum |
0
|
2
|
2
|
| Pennisetum karwinskyi |
0
|
3
|
3
|
| Pennisetum lanatum |
0
|
1
|
1
|
| Pennisetum latifolium |
0
|
38
|
38
|
| Pennisetum longissimum |
0
|
1
|
1
|
| Pennisetum longistylum |
0
|
1
|
1
|
| Pennisetum macrostachyum |
0
|
79
|
79
|
| Pennisetum macrourum |
0
|
33
|
33
|
| Pennisetum monostigma |
0
|
4
|
4
|
| Pennisetum montanum |
0
|
5
|
5
|
| Pennisetum nervosum |
0
|
34
|
34
|
| Pennisetum occidentale |
0
|
38
|
38
|
| Pennisetum pauperum |
0
|
4
|
4
|
| Pennisetum pennisetiforme |
0
|
1
|
1
|
| Pennisetum peruvianum |
0
|
42
|
42
|
| Pennisetum polystachion |
92
|
364
|
456
|
| Pennisetum polystachion subsp. atrichum |
0
|
1
|
1
|
| Pennisetum polystachion subsp. polystachion |
0
|
1
|
1
|
| Pennisetum prolificum |
0
|
13
|
13
|
| Pennisetum purpureum |
36
|
481
|
517
|
| Pennisetum riparium |
1
|
0
|
1
|
| Pennisetum sagittatum |
0
|
2
|
2
|
| Pennisetum schweinfurthii |
3
|
0
|
3
|
| Pennisetum setaceum | 7 | 282 | 289 |
| Pennisetum setigerum |
3
|
0
|
3
|
| Pennisetum sieberianum |
1
|
0
|
1
|
| Pennisetum squamulatum |
2
|
1
|
3
|
| Pennisetum tempisquense |
0
|
2
|
2
|
| Pennisetum thunbergii |
2
|
4
|
6
|
| Pennisetum trachyphyllum |
7
|
2
|
9
|
| Pennisetum tristachyum |
0
|
61
|
61
|
| Pennisetum unisetum |
0
|
13
|
13
|
| Pennisetum villosum |
0
|
228
|
228
|
| Pennisetum weberbaueri |
0
|
4
|
4
|
| Pennisetum divisum |
31
|
61
|
92
|
| Pennisetum mezianum |
5
|
6
|
11
|
| Pennisetum sphacelatum |
9
|
5
|
14
|
| Pennisetum ciliare |
224
|
661
|
885
|
| Pennisetum flaccidum |
5
|
10
|
15
|
| Pennisetum orientale |
28
|
7
|
35
|
| Pennisetum pedicellatum |
117
|
88
|
205
|
| Pennisetum violaceum |
385
|
29
|
414
|
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 66 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)
- Banco Nacional de Germoplasma Vegetal, México (BANGEV, UACH)
- BDBCV - III Semana de la Biodiversidad (Alicante, Spain), 2008
- Biodiversidad de Costa Rica
- Biologiezentrum Linz
- Bishop Museum Natural History Specimen Data
- Bizzenbach-Aue im Bizzenbachtal (Wehrheim/Taunus)
- Bundesamt fuer Naturschutz / Netzwerk Phytodiversitaet Deutschland
- Database Schema for UC Davis [Herbarium Labels]
- EMBRAPA Recursos Geneticos e Biotecnologia - CENARGEN
- EURISCO, The European Genetic Resources Search Catalogue
- Galapagos grasses and sedges
- Haus der Natur Salzburg
- Herbario de la Escuela Nacional de Ciencias Biológicas, México (ENCB, IPN)
- Herbario de la Universidad de Arizona, EUA
- Herbario de la Universidad de Salamanca: SALA
- Herbario del Instituto de Ecología, A.C., México (IE-BAJIO)
- Herbario del Instituto de Ecología, A.C., México (IE-XAL)
- Herbarium de Geo. B. Hinton, México
- Herbarium of Kitakyushu Museum of Natural History and Human History
- Herbarium Specimens of Museum of Nature and Human Activities, Hyogo Pref., Japan
- Herbarium Universitat Ulm
- Herbarium W
- Herbier de la Guyane
- herbier de nouvelle-caledonie
- Hortus Botanicus Sollerensis Herbarium (FBonafè)
- Impetus - Herbarium Hamburgense
- Institut Botanic de Barcelona, BC
- Instituto de Ciencias Naturales
- Internation Botanical Collections (S)
- Inventaire national du Patrimoine naturel (INPN)
- Israel Nature and Parks Authority
- Jardín Botánico de Córdoba: Herbarium COA
- Kurashiki Museum of Natural History
- Lund Botanical Museum (LD)
- Magnoliophyta- Taiwan Biodiversity Data for GBIF
- Missouri Botanical Garden
- New Zealand Biodiversity Recording Network
- New Zealand National Plant Herbarium (CHR)
- NMNH Botany Collections
- NSW herbarium collection
- Observations du Conservatoire botanique national du Bassin parisien.
- Phanerogamie
- Plants of Papua New Guinea
- privater Garten
- Real Jardin Botanico (Madrid), Vascular Plant Herbarium (MA)
- Repatriación de datos del Herbario de Arizona (ARIZ)
- Royal Botanic Gardens, Kew
- SysTax
- The AAU Herbarium Database
- The Deaver Herbarium, Northern Arizona University
- The System-wide Information Network for Genetic Resources (SINGER)
- UA Herbarium
- United States National Plant Germplasm System Collection
- Universidad de Almería, HUAL
- Universidad de Extremadura, UNEX
- Universidad de Málaga: MGC-Cormof
- Universidade Federal de Mato Grosso
- University and Jepson Herbaria DiGIR provider
- USDA PLANTS Database
- USU-UTC Specimen Database
- Vascular Plant Collection
- Vascular Plant Collection - University of Washington Herbarium (WTU)
- Vascular plants of south-central China
Downloads
| Climatic niche model for P. alopecuroide | |
| Climatic niche model for P. bambusiforme | |
| Climatic niche model for P. basedowii | |
| Climatic niche model for P. chilense | |
| Climatic niche model for P. ciliare | |
| Climatic niche model for P. clandestinum | |
| Climatic niche model for P. complanatum | |
| Climatic niche model for P. crinitum | |
| Climatic niche model for P. divisum | |
| Climatic niche model for P. flaccidum | |
| Climatic niche model for P. hordeoides | |
| Climatic niche model for P. latifolium | |
| Climatic niche model for P. macrostachyum | |
| Climatic niche model for P. macrourum | |
| Climatic niche model for P. mezianum | |
| Climatic niche model for P. nervosum | |
| Climatic niche model for P. occidentale | |
| Climatic niche model for P. orientale | |
| Climatic niche model for P. pedicellatum | |
| Climatic niche model for P. peruvianum | |
| Climatic niche model for P. polystachion | |
| Climatic niche model for P. purpureum | |
| Climatic niche model for P. setaceum | |
| Climatic niche model for P. sphacelatum | |
| Climatic niche model for P. tristachyum | |
| Climatic niche model for P. unisetum | |
| Climatic niche model for P. villosum | |
| Climatic niche model for P. violaceum | |
| Pennisetum potential collecting zones | |
| Pennisetum 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 Pennisetum genepool | |
| Dataset used for this analysis |





