In situ and ex situ conservation gap analyses of West African priority crop wild relatives

Crop wild relatives are genetically related wild taxa of crops with unique resources for crop improvement through the transfer of novel and profitable genes. The in situ and ex situ conservation gap analyses for priority crop wild relatives from West Africa were evaluated using species distribution modelling, ecogeographic diversity, and complementary analyses. A total of 20, 125 unique occurrence records were used for the conservation gap analysis, however, 26 taxa had no occurrence data. 64 taxa (62.7%) occurred in protected areas, 56 taxa (55%) were conserved ex situ, while 76.7% (43) of the accessions are underrepresented with less than 50 accessions conserved ex situ. Areas of highest potential diversity were found in the Woroba and Montangnes districts in Cote d’Ivoire, Nzerekore, Faranah, Kindia, and Boke regions of Guinea, South-South, and North-East zones of Nigeria, and Kono and Koinadugu districts in Sierra Leone. Hotspots were found in Atlantique, Littoral, Mono, Kouffo, Atakora, Donga, and Colline provinces of Benin, Accra, and Volta regions of Ghana, North–Central Nigeria, and Lacs district of Cote d’Ivoire and Nzerekore region of Guinea. 29 reserve sites for active in situ conservation were identified, 11 occur in protected areas, while 18 are located outside protected areas. The establishment of the reserve sites will complement existing PAs and ensure long-term active in situ and ex situ conservation and sustainable utilization of priority crop wild relative to underpin food security and mitigate climate change in the region.


Introduction
The flora of West Africa is diverse, heterogeneous, and abundant with numerous plant species. The region harbours over 9000 vascular plants with an estimated 1800 species native to West Africa (Carr et al. 2015). The climate of West Africa is characterized by abundant year-round rainfall in the Gulf of Guinea to a mean annual rainfall of 165 mm in the Agadez of Niger (USGS 2017). Five bioclimate regions have been recognized in West Africa; Saharan, Sahelian, Sudanian, Guinean, and Guinea-Congolian regions (USGS 2017). As such West African plant species are adapted and resilient to the region's erratic, and diverse ecogeographic conditions and may possess useful genes/traits for crop improvement. West Africa is recognized as a region that played a significant role in crop diversity, origin and domestication, and still retains significant crop landraces and CWR diversity (Castañeda-Álvarez et al. 2016;Vincent et al. 2019;Maxted and Vincent 2021). For instance, archaeological records shows that cowpea (Vigna unguiculata (L.) Walp.), originated from Ghana (D'Andrea et al. 2007), kola nut (Kola nitida (Vent.) Schott. and Endl.) originated from West to Central Africa, from Sierra Leone to Congo (Lovejoy 1980), African oil palm (Elaeis guineesis Jacq.) originated from West and Central Africa, from Nigeria and Cameroon to Congo (Carney 2001;Hall 2008), while Coffea canephora Pierre ex A. Froehner (bitter and caffeinated coffee) originated from Central Africa to West Africa (between Congo, Central African Republic, Cameroon, Cote d'Ivoire and Guinea) (Leroy et al. 2014). Similarly, fonio [Digitaria exilis (Kippist) Stapf] was domesticated in Senegal (Harlan 1992) and Pearl millet was domesticated between Mali and Mauritania (Burgarella et al. 2018). The zone between Ghana and Nigeria, down to Cameroon have been identified as the source of yam domestication (Scarcelli et al. 2019), fleshy watermelon [Citrullus lanatus (Thunb.) Matsum. and Nakai] was domesticated in West Africa from C. mucosospermus (Fursa) Fursa (Guo et al. 2013(Guo et al. , 2019Chomicki et al. 2019). Other crops domesticated in West Africa include Garden egg (Solanum macrocarpon L.), Locust bean [Parkia biglobosa (Jacq.) G. Don], Pigeon pea [Cajanus cajan (L.) Millsp], Cotton (Gossypium herbaceum L.), Okra [Abelmoschus esculenta (L.) Moench, Piper seed (Piper guineensis Schumach. and Thonn.), Tamarind (Sesamum indicum L.), and Gourd (Telfairia occidentalis Hook. f.) (MacNeish 1992;Vaughan and Geissler 1999;Carney 2001). Seed cotton, domesticated in West Africa is ranked among the first ten crops in feeding in the world, while watermelon is among the five most economically valuable fruits in the world (FAOSTAT 2020). The extent of crop diversity in West Africa through these crops, has helped to expand the agricultural repertoire beyond the reliance on few global food crops (Champion and Fuller 2018;Kay et al. 2019). The importance of West Africa in terms of crop and intra-crop diversity, and origin and domestication of cultivated crops has recently been recognized by the adding of an additional Vavilov Centre in the west African region (Maxted and Vincent 2021).
Global food production in the next few decades will be determined by several factors including climate change. Climate change will negatively impact agricultural productivity in a global yield decline of an estimated 1.5% per decade (David and Sharon 2012). This trend can at least be partially mitigated by the genetic and agronomic improvement of cultivated crops using trait diversity from crop wild relatives (CWR) (Maxted et al. 2008a, b, c;David and Sharon 2012). CWR are wild plant species relatively closely related to crops, including crop's wild ancestors, that retain indirect use value as gene donors for crop improvement and a high level of genetic diversity having not passed through the genetic bottleneck of domestication. Maxted et al. (2006) defined CWR broadly as all taxa within the same genus as a crop and more precise as wild plant taxon that have indirect use derived from its relatively close genetic relationship to a crop; this relationship is defined in terms of the CWR belonging to gene pools 1 or 2, or taxon groups 1 to 4 of the related crop. CWR contain resilient genes for crop improvement with several domesticated crops in West Africa improved using adaptive genes from CWR (Nduche et al. 2021). Such crops include cassava (David and Sharon 2012;Kawuki et al. 2016), maize (David and Sharon 2012), yam (Lopez-Montes et al. 2012;Saini et al. 2016), cowpea (Andargie et al. 2014;Badiane et al. 2014), millet (Sood et al. 2015), sorghum (Park et al. 2015), rice (Jena 2010;Atwell et al. 2014), barley (Wendler et al. 2015), and for an overview (Nduche et al. 2021).
Despite the important role of CWR in food security in the West African region and the world, their conservation has received little attention. The neglect of CWR is because of lack of appreciation of its potential value in breeding and has resulted in underutilization of its profitable genetic diversity in crop improvement. The adaptive diversity of CWR is a safety net for urgent global food security needs. Globally, in situ conservation of CWR in protected area (PAs) is inadequate, with insufficient number of genetic reserves established . In West Africa, 1938 nationally protected sites exist covering about 9.6% of the region. Another 53 internationally designated protected areas are also found in the region (Mallon et al. 2015). The number of CWR accessions conserved ex situ in genebanks is relatively low compared to accessions of cultivated crops. Globally, there are an estimated 7 million plant accessions conserved in 1750 genebanks (FAO 2010a;Fu 2017), however, about 29% of CWR lack genebank accessions, while over 24% have less than ten accessions represented in genebanks (Castañeda-Álvarez et al. 2016). Despite this shortfall in ex situ conservation of CWR, a comprehensive collection of CWR is still lacking. The combined use of in situ and ex situ conservation of plant genetic diversity will lessen the erosion of valuable genetic diversity (Maxted et al. 1997a;Zegeye 2017).
Despite the wide agreement that in situ and ex situ techniques should be applied in a complementary manner (CBD 1992), almost 100% of CWR diversity when conserved are conserved using ex situ seed storage alone (Maxted et al. 2016). In situ conservation is only recently being implemented and involves the designation of and management of populations to preserve a particular plant species in its natural abode where its intrinsic features are found (Maxted et al. 1997c). To help ensure more ex situ and in situ conservation coverage more recently, gap analysis has been applied for the planning of CWR conservation . It involves identifying CWR diversity that is not well represented in conservation action and prioritizing these 'gaps' for more active conservation (Maxted et al. 2008a;Magos Brehm et al. 2017a;Ng'uni et al. 2019;Mponya et al. 2020;Magos Brehm et al. 2022).
The aim of this study was to undertake in situ and ex situ conservation gap analyses of West African priority CWR, through (a) Evaluating the spatial distribution of West African priority CWR (b) Modelling the predicted distribution of the priority CWR (c) Identifying the reserve sites in PAs for active in situ conservation of priority CWR and locations with inadequate occurrence records (d) Identifying taxa that are not present in PAs and those absent or under-represented in genebanks, for further ex situ collection and effective preservation in genebanks within the region.

Collation and verification of occurrence data
The distributional data for the 102 West African priority CWR defined by Nduche et al. (2021) was collated using a standard occurrence data template (Magos Brehm et al. 2017b). The occurrence data of the West African priority CWR were collated from Global Biodiversity Information Facility (GBIF 2020), Genesys Global Portal on Plant Genetic Resources (Genesys 2020), Royal Botanical Gardens, Kew (https:// www. kew. org/ kew-garde ns), and Rain-Bio (Dauby et al. 2016). A total of 54,924 distributional records were collated for the 102 West African priority CWR. Records that lacked coordinates but with collection sites information were georeferenced, using Google maps (https:// www. maps. google. com). A quality check was done on the distributional data to ensure all records were expressed in decimal degrees. Locational records without decimal degree coordinates were converted to a decimal degree using Canadensys (https:// www. data. canad ensys. net/ tools/ coord inates). Duplicate records were removed before the analysis, and records that lied abnormally in neighbouring countries were reviewed. Duplicate records are distributional records that are associated with the same record but from different sources or was documented twice from the same source (Magos Brehm et al. 2017a). The West African countries included in this study are Benin, Burkina Faso, Cote D' Ivoire, Gambia, Ghana, Guinea, Guinea-Bissau, Liberia, Mali, Mauritania, Niger, Nigeria, Senegal, Sierra Leone and Togo. The 20,125 records without duplicate records were entered in the occurrence data template required by the CAPFITOGEN tool which makes use of the FAO-Biodiversity's multi-crop descriptor (FAO-BIOVERSITY 2015). The 'TesTable tool' of CAPFITOGEN3 was used to verify the occurrence data table to ensure it meets the requirements for other CAPFITOGEN3 tools analyses. GEOQUAL tool of CAPFITOGEN3 was used to assess the quality of coordinates and collection sites of the records (Parra-Quijano et al. 2021).

Ecogeographical land characterization map
Ecogeographic land characterization (ELC) (Parra-Quijano et al. 2021) was used to evaluate the delineation and depiction of ecogeographic variables and determine appropriate sites for in situ and ex situ conservation of priority CWR (Parra-Quijano et al. 2011;Magos Brehm et al. 2022). Eighteen environmental variables (6 bioclimatic, 6 edaphic, and 6 geophysical) were selected in the selecVar tool of CAPFITO-GEN3, to generate the generalist ELC map. A total of 24 ELC zones were produced, which represents the predicted ecogeographic scenarios of the region (Fig. 5) (Parra-Quijano et al. 2012a;Mponya et al. 2020).To accommodate those taxa with distributional records of < 10, a generalist ELC map was generated using the ELC maps tool of CAPFITOGEN3. This is because these taxa cannot generate species -specific ELC map. Using the kmeanbic method, at a resolution of the ecogeographic layer of 10 × 10 km (approximately 5 arc -minutes), the ELC map was created. The kmeanbic method was used because it identifies an optimal number of groups with discriminant analysis of principal components.

Species distribution modelling
Based on environmental layers of various components of ecogeographic variables, predicted taxa distribution was identified by the distribution models produced by the individual taxa with more than 10 occurrence records in Maximum Enthropy Algorithm (MaxEnt) (Phillips et al. 2006) (Table S6). and by circular buffer (CA 50 ) for taxa with less than 10 occurrence records used in the species distribution modelling (SDM), MaxEnt is a common SDM algorithm used to predict taxa distribution (Fourcade et al. 2014). The species distribution data of the taxa for model calibration was classified into a training set (75% of total occurrence data) and test set (25% of total occurrence records) for design evaluation. Raster files of bioclimatic variables were obtained from WorldClim (https:// www. world clim. org/ biocl im), edaphic variables, from ISRIC -World Soil Information (https:// files. isric. org/ soilg rids/), while geophysical data were downloaded as Digital Elevation Map (DEM) files from the National Aeronautics and Space Administration (NASA) (https:// www. nasa. gov.) All ecogeographic raster files were clipped to the same extent, resampled to the same cell size (0.41666666667 m), and reprojected to the same grid (WGS-84), in ASCII raster grid format, using Arc-Map 10.4.1 (ESRI 2015). With Random Forest, integrated in the SelectVar of the CAPFITOGEN tools, variables for each ecogeographic component (bioclimatic, edaphic and geophysical) at resolution of 10 × 10 km (approximately 5 arc minutes at Equator) were selected for each priority taxon (Parra-Quijano et al. 2016). Bivariate correlation analysis was also evaluated in SelecVar, to reduce dimensionality, and only variables with weak correlation (p-value ≤ 0.33) or not correlated (p-value = 0) were used to create the distribution model for each taxon (Tables S7 and S8). Maximum training sensitivity plus specificity threshold was applied, as recommended by Liu et al. (2005). The robustness of the models were evaluated using three criteria: (a) Average area under the test receiver operating characteristics curve [(ATAUC) ˃ 0.7] (b) Standard deviation of ATAUC (STAUC) < 0.15 (c) The proportion of potential distribution area with a STAUC ˃ 0.15, being < 10% were stable and used for evaluating taxa predicted distribution (Ramírez-Villegas et al. 2010; Mponya et al. 2020). All three criteria had to be met for a model to be valid. However, for those taxa that failed the above MaxEnt model validation criteria, and for taxa with occurrence records < 10, predicted distribution were identified by a circular buffer technique, using a radius of 50 km (CA50) around each observational point as recommended by Hijmans and Spooner (2001). In this case, intersecting sites are not counted more than once.

In Situ conservation gap analysis
Gap analysis is a method of evaluation of the extent of conservation which helps to hierarchize CWR for preservation by locating gaps in the conservation (Rodrigues et al. 2004;Langhammer et al. 2007;Magos Brehm et al. 2017a). In situ conservation gap analysis involves a comparative study of intrinsic diversity and the element of diversity that is under active conservation action (Maxted et al. 2008b;Magos Brehm et al. 2017a) The method was described by Maxted et al. (2008a, b, c), Scheldeman and van Zonneveld (2010) and Parra-Quijano et al. (2012b), where in situ and ex situ conservation gap analyses were determined at taxon and ecogeographic levels. At the taxon level, the West African PA map was overlapped with the passport data in QGIS. Subsequently, using 'the join attribute by location' in the 'data management tool' of QGIS, the West African PA maps was intersected to identify records within and outside PA. The in situ conservation gaps were obtained by comparing the number of populations of taxa present in PAs against those not represented in PAs (Mponya et al. 2020). To estimate the extent of representativeness of in situ conservation of priority CWR at the ecogeographic level, the ELC zones from the ELC map tool analysis and the occurrence data were inputted in the 'Representa tool' of CAPFITO-GEN3 (Parra-Quijano et al. 2021). The West African PA maps were overlapped with the ELC maps produced in the 'Representa tool' to determine the representativeness of the ELC zones in PAs.
Complementarity analysis was done to identify potential sites for in situ conservation of priority CWR. Maxted et al. (1997b) described these sites as genetic reserve for long -term active conservation of plant genetic resources. They are defined designated locations either within PAs or outside PAs as informal sites for CWR conservation (Magos Brehm et al. 2017a). Such locations are aimed at conserving a large number of CWR taxa in the smallest available area (Kati et al. 2004). Using the 'Reserve selection' tool in DIVA -GIS 7.5, at resolution of 10 × 10 km (approximately 5 arc minutes), potential genetic reserve sites were identified according to their priority for the conservation of priority CWR. The PA map for West Africa, obtained from UNEP-WCMC (2019) was overlapped with the complementarity genetic reserve site and taxon richness maps to determine the level of current passive in situ conservation of the priority CWR and identify areas that require further active in situ conservation actions. Passive in situ conservation means that CWR in PAs are not actively monitored and managed to preserve their genetic diversity and protect them from pest, diseases, fragmentation, habitat degradation and natural disaster (Vincent et al. 2019). The maps produced were visualized in DIVA-GIS 7.5 (Hijmans et al. 2012) and QGIS 3.16.8 (QGIS-Development Team 2021).

Ex situ conservation gap analysis
Ex situ conservation gap analyses were determined at taxon and ecogeographic levels. At the taxon level, a map of observed ex situ collection was subtracted from the predicted distribution map to obtain the gap in current ex situ conservation and locate the priority site for further ex situ collection. To determine the current germplasm representativeness of the ecogeographic diversity, the resulting ELC map and passport data were inputted in the 'Representa' tool of CAP-FITOGEN to assess the degree of representativeness of the ELC categories in the ex situ collection Team 2021) at a resolution of 10 × 10 km (approximately 5 arc minutes). At the ecogeographic level, the categories of representativeness of the diversity were analysed using the 'Representa tool' of CAP-FITOGEN3 (Parra-Quijano et al. 2021). Based on the frequencies of the ELC map, the ELC map was categorized into quartiles, using the ELC zones in the ELC map. The four frequency classes were low, mid-low, mid-high, and high. However, zones where occurrence records were not found were categorized as 'null'. Ex situ conservation gap were determined by estimating the diversity present in ex situ conservation against that conserved in situ (Mponya et al. 2020;Parra-Quijano et al. 2021).

In situ gap analysis
A total of 20,125 unique occurrence points were used for the in situ conservation gap analysis, however 26 CWR had no occurrence data. The highest occurrence points were recorded in Benin and Nigeria with 31.9% (6428) and 11.7% (2,358) present points, respectively ( Fig. 1 and S1). Hotspots were found in Atlantique, Littoral, Mono, Kouffo, Atakora, Donga and Colline provinces of Benin. These areas correspond to the location of protected areas with the highest number of taxa such as Pendjari (28), Quari Maro (18), La Lama Nord (16), Monts Kouffe and Boucle de la Pendjari (18) (Table S1) There were also hotspots in Accra and Volta regions of Ghana, corresponding to the location of the Volta River reserve site. Location of high diversity were also spotted around Nasarawa, Plateau States of North-Central Nigeria, where Nasarawa Forest Reserve is located and South-Western zone of Nigeria. High species richness is also observed at the Lacs district of Cote d'Ivoire where the Mando forest reserve is situated, Montagnes district of Cote d' Ivoire where Mont Nimba is located and Nzerekore region of Guinea where Mont Nimba, Pic de Fon and Pic de Tibe Classified Forests are located (Fig. 2).
Analysis of the occurrence records showed that 18.5% (3,730) of the total unique present points were recorded in PAs. PAs with the highest number of taxa are Pendjari in Benin (28) Table S1). 62.7% (64) of the priority taxa were represented in a PA, 34.3% (35) of the taxa were present in ≥ 5 PA, while the remaining 27.4% (28) had less than five populations in different PA (Table S2). However, 38 taxa (37.3%) did not occur in any PA. Digitaria cilaris (Retz) Koeler, Vigna racemosa (G. Don) Hutch and Eragrostis pilosa (L.) P. Beauv., had the highest number of taxa populations in PA network with 443, 425 and 234 taxa population, respectively. Similarly, Vigna racemosa (G. Don) Hutch, Eleusine indica (L.) Gaertn. and Oryza glaberrima Steud. occurred in more PAs, appearing in 40, 38 and 37 PAs, respectively, while all the rice crop genepool occurred in the PA network. Cowpea (17), yam (13), and potato (9) crop genepools were the highest number of prioeity taxa that occurred in PA (Table S2). Nigeria, Benin and Cote d' Ivoire had the highest number of PAs where taxa are present, with 46, 25 and 18 PAs, respectively. Conversely, no PA with taxa was identified in Mauritania (Fig. S2). Similarly, the highest number of taxa population in PAs were found in Benin, Burkina -Faso and Cote d'Ivoire had, with 1351, 768 and 463 populations, respectively. Also, Benin, Nigeria and Guinea had the highest number of CWR in PAs, numbering 207, 87 and 76 taxa respectively (Fig. S3)). 38 taxa (37.3%) did not occur in any PA, simimarly none of the Sorghum, fonio and yam wild relatives occurred in PA. Other taxa not represented in PA are Echinochloa crus-galli (L.) P. Beauv., Gossypium herbaceum var. acerifolium (Guill. and Perr.) A. Chev., Ipomoea ochracea (Lindl.) Sweet, Manihot dichotoma Ule, Triticum turgidum L. and Vigna. unguiculata subsp. stenophylla (Harv.) Marechal et al. (Table S2).
Complementarity analysis identified 29 potential genetic reserve sites with grid square size of 0.4 degrees for the conservation of West African priority CWR (Fig. 3). Apart from Burkina -Faso, Liberia, Mauritania and Gambia, genetic reserve sites were identified in all the other West African countries. The highest number of reserve sites were found in Nigeria  (Fig. 3). Eleveen reserve sites are located in PA (Table 1), wth 9 of the sites conserving 37% (38) of the CWR, however priority CWR were absent in Eleiyele and Volta River (Table S1 and S3). A total of 458 records were present in 9 of the reserve sites with taxa. 36.3% (37 taxa) of the priority CWR were found in the reserve sites (Table S3). Vigna racemosa (G. Don) Hutch. and Dalz, Oryza glabarrima Steud, Vigna gracilis (Guill. and Perr.) Hoof. f. and O. barthi A. Chev. had the highest number of taxa population; 56, 51, 46 and 35 respectively in the genetic reserve sites (Table S2  and Table S5). Cowpea (10), yam (7), sweet potato (7), and rice (4), are the crop genepools with the highest number of CWR present in the reserve sites (Table S). Conversely, cowpea (13), yam (8), sweet potato (6) and cassava (5) are the crop genepools with the highest number of taxa not represented in reserve sites. V. racemosa (G. Don) Hutch and Dalz., O. barthi A. Chev., Ipomoea aquatica Forssk., O. longistiminata A. Chev. and Roehr and Eleusine indica (L.) Gaertn were found in more genetic resesrve sites than other taxa and were found in 4 reserve sites each (Table S3 and S5).
In situ conservation gap analysis of the 102 priority CWR showed that the areas of predicted distribution is present in all the West African countries (Fig. 4). The areas of highest potential diversity was found at Woroba and Montangnes districts of Cote d'Ivoire where some protected areas such as Mont Tia, Mont Sangbe, Pic de Fon, Pic de Tibe, Mt Yonon and Mont Nimba reserve site are located (Fig. 4). Also of high predicted CWR taxon richness are Nzerekore, Faranah, Kindia and Boke regions of Guinea where the Mont Nimba and Diecke reserve sites are situated. Other areas of high predicted taxon richness are in the South -South zone of Nigeria around Cross River National Park, North Eastern Nigeria, Kono and Koinadugu districts in Sierra Leone (Fig. 4), where these areas are predicted to harbour 51 to 63 CWR. However, areas from Abidjan in Cote d'Ivoire, Ghana, Togo, Benin to South-West Nigeria had low areas  (Fig. 4). The ecogeographic diversity of 17 ELC zones are present in 152 PAs, while ELC zones 11 and 2 had the higest diversity in PAs (Table S4 and Figs. 5, 6).

Ex situ gap analysis
The SDM of 55 taxa met the validation whereas for the remaining 8 CWR, a CA 50 buffer area created around each occurrence point (Table S6). The number of ecogeographic variables for the SDM varied from

in Vigna filicaulis Hepper and V. desmodiodes
Wilczek to 43 in Ipomoea aquatica Forssk (Table S7 and Table S8). A total of 5720 (28.4%) accessions from 56 (55%) priority CWR are represented ex situ. 13 taxa had occurrence data but did not pass the validation criteria for predicted distribution map    (Fig. S1). Benin had the highest number of occurrence data (6428), while Mauritania had the least (150) (Fig. 1  and Fig. S1).   (Table S9). Similarly, of the 13 taxa that did not occur in PA, 7 were not also represented in genebanks. However, all the taxa with ≥ 50 accessions in genebanks also occurred in ≥ 5 PAs (Table S2 and Table S3). The areas of further collection are found in all the West African countries (Fig. 7), while 87.27% (89) priority CWR needs further collecting (Table S2) (Fig. 7) Ecogeographic diversity of 16 ELC zones are conserved in genebanks (Table S9), while the CWR diversity of 8 zones are not represented. ELC zones 2,8 and 11 had the highest population which corresponds to the ELC map category. 50% of the ELC zones had ≥ 25% of their accessions represented in genebanks (Table S4), while ELC zones 2 and 11 had the highest collection.

Discussion
West Africa is rich with taxa diversity, endemism and biodiversity heritage, while CWR diversity and flora distribution of the region have been reported in various studies (Huchinson and Dalziel 1958;Oates et al. 2004;Bergl et al. 2007;Idohou et al. 2013;Hounsou-Dindin et al. 2022). However, as a purpose of this, further study is needed to determine the gaps in in situ and ex situ conservation action in the region, as this will complement and consolidate the national efforts of the individual countries. According to recent CWR ecogeographic diversity analysis, West Africa has been identified as a region of global importance with high CWR diversity for food security (Castañeda-Álvarez et al. 2016;Vincent et al. 2019). The highest CWR diversity identified in the provinces of Benin, is because of the recent Flora of Benin (Akoègninou et al. 2006), and the high number of occurrence records found in Benin, relative to other countries in the region ( Fig. 1 and S1). High CWR diversity was also identified at Accra and Volta regions of Ghana, North -Central and South-Western zone of Nigeria. Other areas include Lacs district of Cote d' Ivoire and Nzerekore region of Guinea (Fig. 2). These areas correspond to some areas of predicted distribution such as Nzerekore region of Guinea where Mont Nimba, Diecke, Pic de Fon, Pic de Tibe Classified Forests are located (Fig. 4). Similarly, these areas of species richness are in congruence with the Guinean forest, categorized as one of the 36 biodiversity hotspots in the world (Maxted and Vincent 2021;Vincent et al. 2022) and the highest conservation value in Africa (Luiselli et al. 2019). The Guinean Forest covers an area of 621,705 km 2 , extending from Guinea, Sierra Leone, Liberia, Cote d' Ivoire, Ghana, Togo, Benin to Nigeria. However, Guinean Forest is one of the most exploited biodiversity hotspots in the world, though 15% of the original forest is still unexploited (Conservation International 2007).
The network of PAs in West Africa conserves a substantial number of the priority CWR with 61% (63) of the taxa found in PAs (Table S2). However, further field survey should be carried out to ascertain the presence of the priority CWR in those PAs where they were identified. For the 28 taxa (27.4%) that were found in less than five PAs, field survey should be done in areas of predicted distribution to determine their locations and to identify more taxa populations in network of PAs, to ensure they meet or surpass the required minimum number for active in situ conservation. Brown and Briggs (1991) and  suggested the presence of five population of a taxa in different PAs as the minimum for in situ conservation in PA. Also, effective management and monitoring should be put in place to ensure active in situ conservation of the priority CWR in their respective PAs (Maxted et al. 2008b). Relevant institutions, stakeholders, non -governmental organizations (NGOs), and protected area managers should synergistically, ensure the maintenance of the PAs for optimal and active conservation action. Pendjari National Park in Benin with an area of 2765 km 2 and Comoe National Park in Cote d' Ivoire occupying an area of 11,500km 2 are the PAs with the highest number of CWR (Table S1). The presence of more CWR in Pendjari National Park may have resulted from the fact that the site was better surveyed than other PAs, as shown in the number of occurrence data recorded in Benin as compared to other countries ( Fig. 1 and  S1). UNESCO (2019) reported that 620 plant species are found in Comoe National Park, which agrees with the high number of CWR present in Comoe National Park. The site contains great diversity of plants, endemic species and diverse ecological habitats ranging from savannah, forest to grasslands. (UNESCO 2019). Large PAs such as Sahel (30,693 km 2 ), Comoe National Park (11,500 km 2 ), W National Park Benin (10,000 km 2 ), Niokolo -Koba National Park (9130 km 2 ), were design to conserve diverse ecogeographical populations, which CWR is a subset. However, they contain only small of CWR population per unit area. The designation and development of the 18 reserve site found outside PAs, as other effective based conservation measures (OECM) will augment the preservation of CWR population outside PA network .
Identifying priority sites for the in situ conservation of CWR, based on species richness may be misleading since the approach relays only on taxa richness sites neglecting those taxa that require urgent protection (Brooks et al. 2006). However, to overcome this challenge, complementarity analysis through reserve site selection is used (Fielder et al. 2015;Contreras-Toledo et al. 2019;Mponya et al. 2020). Complementarity analysis have been used to identity priority site in regions such as Southern African Development Commission (SADC) (Magos Brehm et al. 2022) and Middle East (Zair et al. 2021). Twenty-nine reserve sites were identified in this study, with 11 in PA and 18 spotted outside PAs. The 11 reserve sites located in PAs will require minimal cost to establish and manage, being in existing PAs. It will augment and complement the protective function offered by the existing PAs and provide benefits to the local communities (Maxted et al. 2008b;Maxted and Kell 2009). The remaining 18 reserve sites not located in PAs also present an opportunity for those countries with low number of PAs where taxa were found such as Guinea -Bissau (3), Mali (4), Niger (5), Sierra Leone (7) and Senegal (9) (Fig. 3). The outcome of the complementary analysis showed that the location of some reserve sites corresponds with some CWR hotspots in West Africa. These areas are Atakora, Alibori, Donga and Bongou provinces in Benin; Accra region of Ghana; North -Central and South -West zones of Nigeria and Lacs district of Cote d' Ivoire (Figs. 2 and 3).
The areas of predicted distribution were highest in Woroba and Montangnes districts of Cote d'Ivoire where the reserve site; Mont Nimba is located and some protected areas such as Mont Tia, Mont Sangbe, Pic de Fon, Pic de Tibe, Mt Yonon are found. The area of high predicted distribution also extended to the Nzerekore, Faranah, Kindia, and Boke regions of Guinea, where the reserve site; Mont Nimba and Diecke Classified Forest are located (Fig. 4). Mont Nimba is strategic because it is located between Guinea and Cote d' Ivoire. It occupies a total land area of 175.4 km 2 , with 125.4 km 2 in Guinea and 50 km 2 in Cote d' Ivoire. UNESCO (2019) reported diverse flora and endemic plant species in the site, including epiphytes and over 2000 vascular plant species. Similarly, Diecke Classified Forest is one of the largest undisturbed areas of the Guinee Forestiere with diverse plant species including several threatened tree species. The presence of Cola attiensis Aubrev. Pellegr. in the site (Table S3) was also reported by (Couch and Haba 2021). The area of predicted distribution appears to be larger than the area of observed distribution, which shows that the region is under surveyed. Efforts should be made for ex situ collection of taxa in predicted areas outside PAs, as they may be under threat by urbanization, change in land use and habitat destruction (Mponya et al. 2020).
For active in situ CWR conservation, effective ex situ conservation is needed to complement it. Ex situ conservation methods include seed bank, genebank, DNA bank, cryopreservation, botanical garden and in-vitro conservation (Maxted et al. 1997c;Maxted 2013). 55% (56) of the priority taxa were represented in genebanks, however more accessions need to be collected for ex situ conservation. Further collection actions should be undertaken for the 20 taxa with occurrence records but not present in genebanks, the 26 taxa without occurrence data and the 44 taxa underrepresented in genebanks to reflect the recommendation by (Brown and Marshall 1995) and (Guerrant et al. 2004) of 50 taxa population for effective representation in genebank. Additionally, taxa already present in PAs should be conserved ex situ in genebanks as a back -up to the in situ conservation to protect them in the event of natural disaster, war or fire outbreak (Ford-Lloyd and Maxted 1993). Genebank accessions should be duplicated regionally and internationally to ensure effective and long term ex situ conservation (FAO 2014;Magos Brehm et al. 2022).
The crop genepools with the highest number of taxa not represented in genebanks are yam (3) (Kawuki et al. 2016). Echinichloa frumentacea Link and Eleusine Africana Kenn -O'Byne are used to breed Barnyard millet (Sood et al. 2015) and finger millet (Dida and Devos 2006), respectively for high yield. Other taxa that are not present in genebanks include Phaseolus vulgaris var. aborigineus (Burkart) Baude, used for the improvement of common bean against bruchid (Osborn et al. 2003), white mould (Mkwaila et al. 2011, web and bacterial blight (Beaver et al. 2012) and for high yield (Wright and Kelly 2011). Sorghum purpureosericeum (Hochst ex. A. Rich) Schweinf and Asch. has confirmed used in the improvement of sorghum for resistance against sorghum shoot fly (Nwanze et al. 1990), while Sorghum bicolor subsp. verticiliforum (L.) Moench is used in breeding sorghum for resistance against stem and leaf rust (Fetch et al. 2009;Park et al. 2015), increase in seed size and weight (Pillen et al. 2004). Hordeum bulbosum L. is used in breeding barley for resistance against barley mild mosaic virus (Ruge et al. 2003;Wendler et al. 2015), barley yellow virus (Wendler et al. 2015), powdery mildew (Pickering and Johnston 2005;Johnston et al. 2009), stem and leaf rust (Fetch et al. 2009;Johnston et al. 2013;Park et al. 2015) and leaf scald (Pickering et al. 2006). Ex situ conservation will be a safety net for some CWR that have their adaptive scenario outside PA. For instance, some herbs and shrubs thrive on lawns, waste lands, swamps and agricultural lands (Maxted and Kell 2009).
A major objective of in situ conservation is to confirm and preserve diverse CWR genes in a defined location for optimal used in crop improvement to ensure food and nutrient security. Ecogeographical diversity can work as proxy for genetic diversity (Korona 1996;Parra-Quijano et al. 2012a). The frequency of ecogeographical diversity outside PAs is higher, compared to that in PA. Therefore, ex situ collection of priority CWR outside PAs will capture taxa in ELC zones not represented or underrepresented in network of PA. The ELC map shows all resilient environmental conditions present within the geographical location of the target taxa population. ELC zone 2 had more accessions in genebanks and the highest frequency of occurrence in PA compared to other ELC categories (Table S4 and Fig. 6). However, taxa found in rare ELC zones present unique genes (Contreras-Toledo et al. 2019;Parra-Quijano et al. 2021) and should be prioritized in ex situ collection and conservation for use in crop improvement of their related crops. Complementarity analysis showed that 11 ELC categories were present in the reserve sites within PA, compared to 15 ELC categories represented in all PAs. This shows a high degree of complementarity in capturing the ecogeographical categories diversity of the priority CWR. On the average, the diversity of ELC categories per taxa was higher (26. 3%) compared to that for all PA network (23.4%) (Table S4). For ELC zones 12,14,16,17,19,22,23,24 where taxa were not represented in genebanks and ELC zones 4,7,20,21 with low genebank representation, based of frequency of occurrence (Table S9), further collection action should be carried out to ensure their representation. Similarly, ex situ collection should be done to represent all the ELC zones and ensure the preservation of novel and vital genes (Rubio-Teso et al. 2013;Parra-Quijano et al. 2021). The presence of these taxa in different ELC zones helps to identify those that thrives in adverse and marginal environments, as they may possess profitable genes for adapting their related crops to erratic climatic conditions (Garcia et al. 2017).

Recommendations
Based on the outcome of this study, the following recommendations for the in situ and ex situ conservation of West African priority CWR are proposed: (1) Improved the efficacy of reserve sites in PAs for active in situ conservation through effective management and monitoring of the target CWR to ensure long term preservation. Small PAs should be expanded to ensure full and optimal conservation area and to include CWR diversity that occurs next to them. The eleven reserve sites in PAs should be prioritized for the in situ conservation of West African priority CWR. Ascertain the suitability of the location of the 18 reserve sites that are not in PA, including the topography, accessibility and demography of the taxa in the area. Then initiate the establishment of reserve sites for the in situ conservation of priority CWR not conserved in PAs, to augment the functions of existing PAs. New PAs are crucial for countries with limited PAs such as Guinea -Bissau, Mali, Niger, Sierra Leone and Senegal ( Fig  S2 and Table S1). The identification of the 29 reserve sites is significant and a footprint for the in situ conservation of the priority CWR.
(2) Conduct field survey for the 38 taxa that did not occur in PA to ensure they are present in at least five PAs to meet the minimum number of representations in PAs for active in situ conservation   (Table S10) and conserved in area where the taxa have their intrinsic features and taxon richness. (4) Search for occurrence data for the 26 taxa without occurrence records and for those with less than 10 records in their countries of endemism. Conduct field survey for countries with inadequate number of occurrence data such as Mauritania, Gambia, Guinea -Bissau, Liberia, Togo and Sierra Leone (Fig. S1), to identify the location of more priority CWR and taxa population both within and outside PAs for ex situ collection and active in situ conservation. SDM and buffer CA 50 can serve as a guide in locating the taxa in the areas of predicted distribution. (5) Prioritize the ex situ collection of the 43 taxa with less than 50 accessions in genebanks, using the SDM and CA 50 as a guide to ensure their effective representation ex situ. Also, of priority are the 13 taxa with occurrence data but did not pass the validation criteria. Diversity in ex situ conservation should be increased to include seed banks, cryopreservation, in -vitro storage for recalcitrant taxa, and botanical garden. Government agencies, institutions, local communities, national and international genebanks should be involved in the collection mission.
(6) Conduct field survey to identify priority CWR in the ELC zones with low frequency to ensure that a full range of ELC zones are captured so as to preserve unique and novel genes for use in crop improvement (Parra-Quijano et al. 2021). (7) Make crosses between plants from collected seeds and their related crops, as well as between CWR found in PA and their related crops based on genepool levels (Table S11). Advanced methods such as embryo rescue, in-vitro gene transfer can be used for CWR that shows difficulty with conventional methods. This may help in resolving the challenge of hunger and food insecurity in the densely populated West African region. (8) Periodic revision, review and upgrade of the outcome of this study and the recommendations in the event of change in conservation priorities as a result of availability of more occurrence records and a more precise algorithm for ecogeographic modelling and occurrence data analysis.

Conclusion
In this study, the in situ and ex situ conservation gaps for the 102 West African CWR were evaluated. The 26 taxa without occurrence data, 20 taxa with occurrence records but not present in genebanks, and the 44 taxa underrepresented in genebanks have been prioritized for further ex situ collection to ensure their effective representation in genebanks. The areas of high predicted distribution within PAs such as Mont Tia, Mont Sangbe, Pic de Fon, Pic de Tibe, Mt Yonon, Cross River National Park and reserve site such as Mont Nimba and Diecke were also prioritized for ex situ collection. The 38 taxa that are not present in PA and the 28 taxa with less than five population in different PAs were also target taxa for identification and in situ conservation action. Establishment of the 29 identified reserve sites will further strengthen the CWR in situ conservation effort at national and regional level. Similarly, filling the identified in situ and ex situ conservation gaps will ensure that the priority CWR and agrobiodiversity are availability for use as food, feed and fibre. Additionally, the implementation of the proposed recommendations will enhance the active conservation and sustainable utilization of the priority CWR for crop improvement to mitigate climate change and underpin food security for the rising population in West Africa.