High priority taxa
Following taxa (55 out of 84) were found to be high priority taxa to collect:
- P. albiflorus
- P. albiviolaceus
- P. altimontanus
- P. amabilis
- P. amblyosepalus
- P. anisophyllus
- P. carteri
- P. chacoensis
- P. chiapasanus
- P. coccineus subsp. coccineus
- P. coccineus subsp. darwinianus
- P. coccineus subsp. formosus
- P. coccineus var. griseus
- P. coccineus subsp. striatus var. purpurascens
- P. diversifolius
- P. elongatus
- P. esperanzae
- P. esquincensis
- P. falciformis
- P. formosus
- P. fraternus
- P. galactoides
- P. jaliscanus
- P. laxiflorus
- P. leptostachyus var. intonsus
- P. leptostachyus var. leptostachyus
- P. leptostachyus var. nanus
- P. macrolepis
- P. macvaughii
- P. marechalii
- P. micranthus
- P. mollis
- P. nelsonii
- P. novoleonensis
- P. oaxacanus
- P. opacus
- P. pachycarpus
- P. pauper
- P. perplexus
- P. plagiocylix
- P. polymorphus
- P. polystachios
- P. polystachios subsp. smilacifolius
- P. reticulatus
- P. ritensis
- P. rosei
- P. rotundatus
- P. salicifolius
- P. sonorensis
- P. tenellus
- P. tenuifolius
- P. texensis
- P. trifidus
- P. venosus
- P. xolocotzii
See the priorities list here
Identified gaps for Phaseolus genepool
(see downloads)
El género Phaseolus comprende alrededor de 50 especies (Debouck, 1988), en donde las especies P. vulgaris (frijol común), P. coccineus (ayocote), P. acutifolius (frijol tépari), P. dumosus (frijol cacha) y P. lunatus (frijol Lima) corresponden a las especies cultivadas. La organización de la diversidad genética en el género Phaseolus está basada en la habilidad de las especies de cruzarse con P. vulgaris, se ha sugerido que tal organización está dividida en cuatro acervos genéticos diferentes de acuerdo a relaciones filogenéticas (Smartt, 1980; Singh and Jauhar, 2005), como se muestra en la siguiente tabla:
|
Primary genepool
|
Secondary genepool
|
Tertiary genepool
|
Quaternary genepool
|
|
P. vulgaris cultivars, landraces and wild specimens
|
P. coccineus
|
P. acutifolius
|
P. lunatus
|
|
P. polyanthus (syn. P. dumosus)
|
P. parvifolius
|
||
|
P. costaricensis
|
We have gathered data from different sources: the Global Biodiversity Information Facility (GBIF), the System-wide Information Network for Genetic Resources (SINGER) and the Genetic Resources Information Network (GRIN). We found data for 70 wild species and 14 infraspecific taxa, accounting to a total of 84 taxa for analysis.
The analysis dataset (download) contained 5,146 observations, with 2,879 (56%) being herbarium specimens and 2,267 (44%) being genebank accessions. The average number of total samples per taxon was 61 (standard deviation of 148), indicating that available data is relatively abundant, although it is concentrated in certain taxa (i.e. P. acutifolius, P. angustissimus, P. coccineus, P. filiformis, P. leptostachyus, P. lunatus, P. polystachios, P. vulgaris). Other taxa such as P. albiviolaceus (1), P. fraternus (1) and P. micranthus (1), 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 Phaseolus genepool showed that there are 55 taxa that are either underrepresented or not represented in any way in genebanks out of the 84 taxa under analysis and these taxa were therefore flagged as high priority species. 49 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. P. albiviolaceus, P. amabilis, P. chacoensis, P. diversifolius, P. elongatus, P. fraternus, P. laxiflorus, P. micranthus, P. mollis, P. ritensis, P. opacus, P. pachycarpus). There are some taxa such as P. coccineus subsp. coccineus, P. coccineus var. griseus, P. coccineus subsp. darwinianus, P. coccineus subsp. formosus, P. coccineus subsp. striatus var. purpurascens that were flagged as high priority taxa, but they appear to be a classification issue rather than being a conservation issue (as P. coccineus was found to be well conserved ex-situ); and the same happens with P. leptostachyus var. intonsus and P. leptostachyus var. nanus.
Potential sampling zones
Phaseolus high priority taxa were found to be mostly distributed in Central America. 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
The greatest sampling-richness was found in Mexico.
Brief description of data used in the analysis
The table below shows the number of records (herbarium, germplasm, total) used per species for the Phaseolus genepool gap analysis.
|
Species
|
Genebank accessions
|
Herbarium samples
|
Total
|
| Phaseolus albiflorus |
5
|
0
|
5
|
| Phaseolus albiviolaceus |
0
|
1
|
1
|
| Phaseolus altimontanus |
2
|
1
|
3
|
| Phaseolus amabilis |
0
|
1
|
1
|
| Phaseolus amblyosepalus |
0
|
10
|
10
|
| Phaseolus anisophyllus |
0
|
2
|
2
|
| Phaseolus carteri |
5
|
2
|
7
|
| Phaseolus chacoensis |
0
|
1
|
1
|
| Phaseolus chiapasanus |
6
|
5
|
11
|
| Phaseolus coccineus subsp. coccineus |
0
|
35
|
35
|
| Phaseolus coccineus subsp. darwinianus |
0
|
1
|
1
|
| Phaseolus coccineus subsp. formosus | 0 | 3 | 3 |
| Phaseolus coccineus var. griseus |
0
|
1
|
1
|
| Phaseolus coccineus subsp. striatus var. purpurascens |
2
|
0
|
2
|
| Phaseolus diversifolius |
0
|
1
|
1
|
| Phaseolus elongatus |
0
|
1
|
1
|
| Phaseolus esperanzae |
1
|
1
|
2
|
| Phaseolus esquincensis |
0
|
4
|
4
|
| Phaseolus falciformis |
0
|
3
|
3
|
| Phaseolus formosus |
0
|
7
|
7
|
| Phaseolus fraternus |
0
|
1
|
1
|
| Phaseolus galactoides |
4
|
10
|
14
|
| Phaseolus jaliscanus |
1
|
5
|
6
|
| Phaseolus laxiflorus |
0
|
1
|
1
|
| Phaseolus leptostachyus var. intonsus |
0
|
1
|
1
|
| Phaseolus leptostachyus var. leptostachyus |
0
|
50
|
50
|
| Phaseolus leptostachyus var. nanus |
0
|
1
|
1
|
| Phaseolus macrolepis |
3
|
1
|
4
|
| Phaseolus macvaughii |
2
|
4
|
6
|
| Phaseolus marechalii |
1
|
1
|
2
|
| Phaseolus micranthus |
1
|
0
|
1
|
| Phaseolus mollis |
0
|
1
|
1
|
| Phaseolus nelsonii |
0
|
28
|
28
|
| Phaseolus ritensis |
0
|
1
|
1
|
| Phaseolus novoleonensis |
2
|
2
|
4
|
| Phaseolus oaxacanus |
0
|
2
|
2
|
| Phaseolus opacus |
0
|
1
|
1
|
| Phaseolus pachycarpus |
0
|
1
|
1
|
| Phaseolus pauper |
0
|
2
|
2
|
| Phaseolus perplexus |
1
|
7
|
8
|
| Phaseolus plagiocylix |
0
|
2
|
2
|
| Phaseolus polymorphus |
1
|
5
|
6
|
| Phaseolus polystachios |
1
|
323
|
324
|
| Phaseolus polystachios subsp. smilacifolius |
0
|
2
|
2
|
| Phaseolus reticulatus |
1
|
4
|
5
|
| Phaseolus rosei |
0
|
2
|
2
|
| Phaseolus rotundatus |
2
|
1
|
3
|
| Phaseolus salicifolius |
1
|
2
|
3
|
| Phaseolus sonorensis |
0
|
2
|
2
|
| Phaseolus tenellus |
0
|
4
|
4
|
| Phaseolus tenuifolius |
0
|
2
|
2
|
| Phaseolus texensis |
1
|
0
|
1
|
| Phaseolus trifidus |
0
|
1
|
1
|
| Phaseolus venosus |
0
|
6
|
6
|
| Phaseolus xolocotzii |
0
|
1
|
1
|
| Phaseolus acutifolius |
29
|
7
|
36
|
| Phaseolus acutifolius var. acutifolius |
119
|
64
|
183
|
| Phaseolus acutifolius var. tenuifolius |
152
|
98
|
250
|
| Phaseolus coccineus |
283
|
273
|
556
|
| Phaseolus costaricensis |
14
|
46
|
60
|
| Phaseolus filiformis |
58
|
307
|
365
|
| Phaseolus glabellus |
10
|
10
|
20
|
| Phaseolus grayanus |
30
|
28
|
58
|
| Phaseolus leptostachyus |
76
|
135
|
211
|
| Phaseolus lunatus |
181
|
279
|
460
|
| Phaseolus maculatus subsp. ritensis |
31
|
94
|
125
|
| Phaseolus oligospermus |
11
|
21
|
32
|
| Phaseolus parvifolius |
34
|
42
|
76
|
| Phaseolus pauciflorus |
2
|
105
|
107
|
| Phaseolus talamancensis |
1
|
17
|
18
|
| Phaseolus angustissimus |
11
|
211
|
222
|
| Phaseolus maculatus subsp. maculatus |
21
|
128
|
149
|
| Phaseolus parvulus |
11
|
73
|
84
|
| Phaseolus pedicellatus |
5
|
63
|
68
|
| Phaseolus pluriflorus |
7
|
43
|
50
|
| Phaseolus tuerckheimii |
3
|
17
|
20
|
| Phaseolus augusti |
54
|
20
|
74
|
| Phaseolus dumosus |
94
|
85
|
179
|
| Phaseolus maculatus |
12
|
0
|
12
|
| Phaseolus neglectus |
8
|
7
|
15
|
| Phaseolus pachyrrhizoides |
21
|
3
|
24
|
| Phaseolus vulgaris |
893
|
133
|
1026
|
| Phaseolus xanthotrichus |
26
|
8
|
34
|
| Phaseolus zimapanensis |
27
|
5
|
32
|
Species’ taxonomy was reviewed using Maxted and Kell (2009) as a first stage, the GRIN taxonomical review in second place. 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 34 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
- Biodiversidad de Costa Rica
- California State University, Chico
- CIAT-Genetic Resources Unit
- Colecciones de George Boole Hinton depositadas en el herbario de Kew: Familia Leguminosae
- Daniel Debouck - Cahiers de Phaséologie
- DAO Herbarium Type Specimens
- Ejemplares tipo de plantas vasculares del Herbario de la Escuela Nacional de Ciencias Biológicas, México (ENCB, IPN)
- Fairchild Tropical Botanic Garden Virtual Herbarium Darwin Core format
- Freytag and Debouck (2002)
- GRIN
- Harvard University Herbaria
- Herbario de la Universidad de Arizona, EUA
- Herbario del Instituto de Ecología, A.C., México (IE-BAJIO)
- Herbarium (UNA)
- Herbarium de Geo. B. Hinton, México
- Herbier de la Guyane
- Instituto de Ciencias Naturales
- ITIS
- Missouri Botanical Garden
- National Botanic Garden of Belgium (NBGB)
- National Vegetable Germplasm Bank, Mexico (BANGEV)
- Native Seeds/SEARCH (NSS)
- New York Botanical Garden (NYBG)
- NMNH Botany Collections
- Phanerogamie
- Repatriación de datos del Herbario de Arizona (ARIZ)
- Royal Botanic Gardens, Kew
- The AAU Herbarium Database
- The Deaver Herbarium, Northern Arizona University
- United States National Plant Germplasm System Collection
- USDA PLANTS Database
- Vascular Plant Type Specimens
Downloads
| Climatic niche model for P. acutifolius var. acutifolius | |
| Climatic niche model for P. acutifolius var. tenuifolius | |
| Climatic niche model for P. acutifolius | |
| Climatic niche model for P. amblyosepalus | |
| Climatic niche model for P. angustissimus | |
| Climatic niche model for P. augusti | |
| Climatic niche model for P. coccineus subsp. coccineus | |
| Climatic niche model for P. coccineus | |
| Climatic niche model for P. costaricensis | |
| Climatic niche model for P. dumosus | |
| Climatic niche model for P. filiformis | |
| Climatic niche model for P. glabellus | |
| Climatic niche model for P. grayanus | |
| Climatic niche model for P. leptostachyus subsp. leptostachyus | |
| Climatic niche model for P. leptostachyus | |
| Climatic niche model for P. lunatus | |
| Climatic niche model for P. maculatus subsp. maculatus | |
| Climatic niche model for P. maculatus subsp. ritensis | |
| Climatic niche model for P. maculatus | |
| Climatic niche model for P. neglectus | |
| Climatic niche model for P. nelsonii | |
| Climatic niche model for P. oligospermus | |
| Climatic niche model for P. pachyrrhizoides | |
| Climatic niche model for P. parvifolius | |
| Climatic niche model for P. parvulus | |
| Climatic niche model for P. pauciflorus | |
| Climatic niche model for P. pedicellatus | |
| Climatic niche model for P. pluriflorus | |
| Climatic niche model for P. polystachios | |
| Climatic niche model for P. talamancensis | |
| Climatic niche model for P. tuerckheimii | |
| Climatic niche model for P. vulgaris | |
| Climatic niche model for P. xanthotrichus | |
| Climatic niche model for P. zimapanensis | |
| Phaseolus potential collecting zones | |
| Phaseolus 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 Phaseolus genepool | |
| Dataset used for this analysis |






Hi,
I´m Jorge Berny. A researcher of INIFAP in Yucatan, Mexico. I work mainly on genetics and breeding of Capsicum, and Phaseolus (vulgaris and Lunatus) and Vigna. I´ll be starting a GCDT sponsored project about terminal drought and begomivirus resistance of the Yucatan peninsula bean landraces. Anyway, just to let you know that there is great variability in the cultivated (maize-bean system) and wild phaseolus vulgaris and lunatus. We have several accesions in our collection and also further collection activities could be very valuable. I´ll be more than glad to collaborate. Also in Capsicum if you are interested.
With regards,
Jorge C. Berny
Great to hear that Jorge!. We’re developing also Gap Analyses on cropped accessions (landraces, breeding materials), so, besides passport data (which is key for us), any characterization, or genetic level data would be very useful to us (either from wild species or cropped accessions).
As we are also interested on validation of our method, it would be great any further collection plans and their respective results. We appreciate your interest and will look forward for any input data you may be able to provide on both wild species or cropped accessions. We have georreferencing and correction tools, so, if you are lack of lat/lon data but have collection site names (locality and municipalities names) we could add the coordinates via our tools and then give you the data back.
Let us know how do you want to move forward on this. If needed, you can write directly to Nora and/or me (in the contact us link just at the top-right of the page).
Wonderful resource. One thing; the View in google Earth link does not work for me. I get error “This Virtual Directory does not allow contents to be listed.”
Thanks.