Abstract
Wild edible plants are still eaten by a large section of the global population and ensure both affordable food and nutritional security. We tested this in an Indian context, where an enormous diversity of such plants constitutes a significant part of the rural diet and their acceptance has been high. In this study, we assessed the diversity of wild edible plant resource and the importance of species based on the use and its pattern. We have also shortlisted a set of plants to make an informed decision on prioritization. We found a great variety of plants (1,403 species) from 184 families were consumed across India, although the first 44 families (24%) contributed largely to the (75%) diversity. Leguminosae followed by Compositae, Poaceae, Malvaceae, and Rosaceae, were the families with the highest number of species. We note that a few species from the large pool were extensively used throughout the country while another few were valued for their multiple edible plant parts. Leafy shoots (722 species) followed by fruits (652 species) were the two most-eaten plant parts. Our results strengthen the fact that: (a) wild edibles have been an integral part of the diet; (b) their widespread assimilation into local food culture suggests an untapped potential to ensure easy availability and access to micronutrients for sustainable food systems, and thus in social welfare; and (c) they should be incorporated into the national food policy for formal cultivation and promotion.
Introduction
Food has been central to human biological and socio-cultural existence, providing energy and nutrition. Sourcing food from the wild had been closely entangled with humanity for millions of years (Gosden and Hather, 2004). It allowed humans to develop an intricate knowledge base about the environment and provided them with a diverse collection of animal and plant derived foods, procured through numerous ingenious ways (Anderson et al., 2011; Chevalier et al., 2014a; Harris and Hillman, 2014). Today, nearly thirty domesticated species comprise a significant portion of dietary diversity and only three principal cereal grains (rice, wheat, and maize) contribute to more than half of the world's calorie intake (FAO, 2010). Thousands of edible species remained wild or semi-wild, and were left-out in the course of domestication; however, these underutilized edible floral elements hold the potential to transform our food systems toward being more nutritious, sustainable, and resilient to climate change (Hunter and Fanzo, 2013; Powell et al., 2015). A diverse range of wild uncultivated plants and their parts (e.g., leafy shoots, fruits, seeds, underground organs, and flowers) are still being consumed regularly and complement human adaptability and a variety of human gastronomic choice. They tend to supplement proteins, essential minerals, micronutrients, and vitamins that enrich dietary quality (Ogle, 2001) and thus provide an affordable source of nutrition for rural and semi-urban societies across cultures and continents (Rowland et al., 2016; Jones, 2017). Diverse diets have largely been recommended for optimum human nutrition, good health, and overall well-being (FAO et al., 2012). While poor quality staple-centric diets lacking diversity may represent the diets of most low-income households in low- and middle-income countries (Jones, 2017), the acceptance and use of wild food is vibrantly alive to this day, especially in remote economically impoverished corners of the world (Christiensen, 2002; Lykke et al., 2002; Paumgarten and Shackleton, 2011; Cruz-Garcia and Price, 2012; Angelsen et al., 2014; Wunder et al., 2014; Ickowitz et al., 2016). However, the exponential growth of industrial agriculture, rapid urbanization, and the dwindling of forest and semi-forest lands have heavily affected the food system (Padoch and Sunderland, 2014; Broegaard et al., 2017; Ickowitz et al., 2019). The obvious consequences are the decimation of wild populations and loss of the knowledge system required to harvest and process these foods, which eventually led to food system homogenization, micronutrient deficiency, undernourishment, and over-nutrition manifesting in overweight or obesity (Pretty, 1995; Labadarios, 2005; Pinstrup-Andersen, 2007; Pingali, 2015).
The culture of consumption of wild edible plants (henceforth WEP) as food and medicine has been widely exercised by the tribal groups and non-tribal communities living in rural and semi-urban settings. In particular, the availability of plants collected from anthropogenic landscapes (i.e., the vicinity of rice fields, homesteads, forest patches, or fallow lands) and their easy access have often allowed a large fraction of people to depend on them as a valuable nutritional resource. In spite of an unprecedented diversity of WEP in India and their widespread consumption, comprehensive studies describing the general pattern are almost absent, e.g., what is the extent of the diversity of wild food spectra? What are the frequently used taxa? How does the pattern of consumption change with geography? Isolated studies have explored the taxonomic diversity, the part(s) used, and the method of processing before consumption, but stopped short of linking the findings with a larger country-wise pattern, which are crucial to perceive the magnitude of dependence on the wild resources and its implication for the usage of WEPs to be incorporated into food policy in order to make it more sustainable. In this study, we collected data to answer the following questions: (i) what is the taxonomic diversity of WEPs and their family-wise distribution? (ii) what is the pattern of use by parts? and (iii) how could an informed-decision be made to prioritize for policy on nutritional security?
Materials and Methods: (Details in Supplementary Methods S1)
Study Plan, Data, and Source
The studies suggest that the WEPs or their habitat are always under minimal to moderate direct or indirect manipulation (Turner et al., 2011). So, we adhered to this inclusive definition to consider WEP in our study and we have shortlisted 105 published articles describing the consumption of wild flora (Figure 1, Table 1). We carefully made the selection so that a fair representation of the food plant choice of the Indian subcontinent is reflected in our choice. We have tabulated the wild plant species, family, part(s) used, geographic location of the study, and the consuming communities. Species identity was confirmed through The Plant List (2010).
Figure 1
Table 1
| References | Broad region |
|---|---|
| Agrahar-Murugkar and Subbulakshmi (2005) | North-east |
| Ajesh et al. (2012) | South |
| Angami et al. (2006) | North-east |
| Arinathan et al. (2007) | South |
| Ayyanar and Ignacimuthu (2005) | South |
| Barua and Tomar (2014) | Central |
| Bedi (1978) | West |
| Behera et al. (2008) | East |
| Bhatt et al. (2005) | North-east |
| Binu (2010) | South |
| Biswas and Das (2011) | East |
| Chaithanya et al. (2015) | South |
| Chand et al. (2017) | North |
| Chauhan et al. (2014) | Central |
| Chauhan et al. (2018) | West |
| Chorol et al. (2018) | North |
| Choudhary et al. (2008) | West |
| Cruz-García (2006) | South |
| Devi et al. (2010) | North-east |
| Devi et al. (2014) | North-east |
| Devi and Salam (2016) | North-east |
| Fatma and Pan (2012) | East |
| Gangte et al. (2013) | North-east |
| Ghatapanadi et al. (2011) | South |
| Ghosh-Jerath et al. (2015) | East |
| Ghosh-Jerath et al. (2016) | East |
| Horo and Topno (2015) | East |
| Ignacimuthu and Ayyanar (2006) | South |
| Jain and Tiwari (2012) | Central |
| Jain et al. (2011) | North-east |
| Jain et al. (2012) | North-east |
| Jain (1964) | Central |
| Jeeva (2009) | North-east |
| Kar (2004) | North-east |
| Kar and Borthakur (2007) | North-east |
| Kar and Borthakur (2008) | North-east |
| Katewa et al. (2003) | West |
| Khan and Kakde (2014) | South |
| Khaund and Joshi (2013) | North-east |
| Konsam et al. (2016) | North-east |
| Kumar (2013) | North |
| Kumar and Shiddamallayya (2014) | South |
| Kumar and Jain (2002) | Central |
| Mahapatra and Panda (2012) | East |
| Maikhuri et al. (1994) | North |
| Mao et al. (2009) | North-east |
| Medhi and Borthakur (2012) | North-east |
| Medhi et al. (2014) | North-east |
| Mishra et al. (2016) | East |
| Mishra and Shrivastava (2015) | Central |
| Misra et al. (2013) | East |
| Misra et al. (2008) | North |
| Mohammed et al. (2004) | West |
| Mukherjee and Chaturvedi (2016) | East |
| Murugan et al. (2010) | North |
| Nair and Agrawal (2017) | Central |
| Namsa et al. (2011) | North-east |
| Nath and Maiti (2011) | North-east |
| Neogi et al. (1989) | North-east |
| Nongdam and Tikendra (2014) | North-east |
| Narayanan et al. (2011) | South |
| Nazarudeen (2010) | South |
| Padalia (2015) | North |
| Panda (2014) | East |
| Pandey (1998) | North |
| Pandey and Saini (2007) | Central |
| Pandey and Pande (2016) | North |
| Pandey et al. (2015) | North-east |
| Pandey and Bora (1997) | North-east |
| Pant and Samant (2010) | North |
| Parinitha et al. (2004) | South |
| Parisara and Kiran (2016) | South |
| Patiri and Borah (2007) | North-east |
| Phoze et al. (2001) | North-east |
| Pradhan and Badola (2008) | East |
| Radha et al. (2013) | North |
| Rajasab and Isaq (2004) | South |
| Ramachandran (2007) | South |
| Ramachandran et al. (2009) | South |
| Rana et al. (2012) | North |
| Rasingam (2012) | South |
| Samydurai et al. (2012) | South |
| Sasi et al. (2011) | South |
| Sasi and Rajendran (2012) | South |
| Sarvalingam et al. (2015) | South |
| Sathyavathi and Janardhanan (2014) | South |
| Satyavani et al. (2015) | South |
| Singh A. et al. (2013) | Central |
| Singh B. K. et al. (2013) | North-east |
| Singh et al. (2014) | North |
| Singh et al. (2011) | North-east |
| Sinha and Lakra (2007) | East |
| Srivastava (1998) | North |
| Sundriyal and Sundriyal (2001) | East |
| Sundriyal and Sundriyal (2003) | East |
| Suthari et al. (2014) | South |
| Swarnkar and Katewa (2008) | West |
| Thomas et al. (2011) | Central |
| Tiwari et al. (2010) | North |
| Upreti et al. (2010) | North |
| Vikneshwaran et al. (2008) | South |
| Vishwakarma and Dubey (2011) | Central |
| Yakang et al. (2013) | North-east |
| Yuhlung and Bhattacharyya (2014) | North-east |
| Yumnam et al. (2011) | North-east |
The list of studies and their broadly studied region.
Taxonomic Diversity, Distribution of Wild Edible Plants, and Use-Frequency
We determined the diversity of food plants and evaluated species distribution across families. Further, in order to gain an insight into how the families contribute to the total species pool (number of species), we plotted total species (%) against the number of families. In order to assess the popularity of a species, relative frequency of citation (RFC) was calculated.
The Pattern of Use by Parts
To gain an understanding of the use by parts, the total species pool is divided into six broad categories depending on the edible parts documented, i.e., seeds or grains, leaves and leafy shoots (including pteridophytes), flowers, fleshy fruits, underground parts (including true roots or various below-ground storage organs, such as, bulbs, corms, tubers, and rhizomes), and the others broadly following the classification by Turner et al. (2011). The creation of a sixth heterogenous group as “others” included plant parts other than first five, e.g., aril, bark, cambium, peduncle, sap, bulbil, fruit body, petiole, pith, etc. Further, we also examined species distribution across families separately for each of the plant parts.
In order to uncover the importance of a species in terms of its edible parts, we have calculated the relative use value (RUV) of a selected set of species whose number of edible parts were equal to or >3. In addition, we have also determined consensus value for plant part (CPP) for selected high-ranking species derived from RUV and RFC values.
Prioritization
We sought to shortlist species building on information captured in two indices, RFC and RUV; it allowed us to formulate a scientifically-informed way of selecting a few from a large pool that could enable policy formulation.
Results
Taxonomic Diversity of Wild Edible Plants and Use-Frequency Spectra
We found a total of 1,403 species belonging to 184 families (Table 2, Supplementary Table 1). In terms of species count, Leguminosae ranked first with 119 species with Compositae (57), Poaceae (53), Malvaceae (49), Rosaceae (48), Rubiaceae (42), Lamiaceae (41), Moraceae (39), Amaranthaceae (38), and Araceae (32) following it (Figure 2). When the species count was plotted against the number of families, it showed the top 17 families (9.2% of the total families) contributed to nearly 50% (646 species) and the first 44 families (23.9% of the families) captured about 75% (971 species) of the total species count (Figure 3).
Table 2
| Plant parts | Family | Species |
|---|---|---|
| Total | 184 | 1,403 |
| Seeds | 39 | 155 |
| Leaves or shoots | 134 | 740 |
| Flowers | 59 | 153 |
| Fruits | 110 | 657 |
| Underground parts | 70 | 219 |
| Others | 69 | 167 |
Taxonomic diversity of the edible species, total and part-based.
Figure 2
Figure 3
RFC value segregated species based on their mentioned use in the number of studies and it varied from 0.012 to 0.46 (Table 3A). For instance, Oxalis corniculata, Amaranthus spinosus, Phyllanthus emblica, Colocasia esculenta, and Solanum americanum were the top five species with citation-frequencies of 0.46, 0.393, 0.371, 0.348, and 0.348, respectively.
Table 3A
| Species | Number of studies mentioning use | RFC |
|---|---|---|
| Oxalis corniculata | 41 | 0.39 |
| Amaranthus spinosus | 35 | 0.33 |
| Phyllanthus emblica | 33 | 0.31 |
| Colocasia esculenta | 31 | 0.295 |
| Solanum americanum | 31 | 0.295 |
| Centella asiatica | 31 | 0.295 |
| Amaranthus viridis | 29 | 0.28 |
| Chenopodium album | 28 | 0.27 |
| Dioscorea bulbifera | 27 | 0.26 |
| Commelina benghalensis | 26 | 0.25 |
| Alternanthera sessilis | 26 | 0.25 |
| Dioscorea pentaphylla | 26 | 0.25 |
| Ziziphus jujuba | 24 | 0.23 |
| Portulaca oleracea | 23 | 0.22 |
| Senna tora | 22 | 0.22 |
| Boerhavia diffusa | 22 | 0.22 |
| Ipomoea aquatica | 22 | 0.22 |
| Ficus racemosa | 21 | 0.2 |
| Tamarindus indica | 21 | 0.2 |
| Asparagus racemosus | 21 | 0.2 |
| Aegle marmelos | 21 | 0.2 |
| Diplazium esculentum | 21 | 0.2 |
| Solanum torvum | 20 | 0.19 |
| Moringa oleifera | 19 | 0.181 |
| Spondias pinnata | 19 | 0.181 |
A list of species with high RFC value (up to 50% of the maximum).
The Pattern of Use by Parts
On grouping total species according to the edible plant parts, the highest number of species seemed to be used as leafy greens (740 species from 134 families). Consumption as fruits ranked next to it (657 species from 110 families), followed by seeds, underground parts, and flowers (Table 2). When analyzed at a family level, Leguminosae was a highly speciose food plant family and topped the list in most of the categories, i.e., leaves-shoots (60 species), seeds (47 species), and flowers (27 species). In the other two categories, fruits and underground parts, Rosaceae (52 species) and Dioscoreaceae (23 species) had the highest number of edible species, respectively (Figures 4A–E).
Figure 4
The range of relative use-value (RUV) varied from 0.5 to 1, however, only one species, Nymphaea nouchali demonstrated a RUV of one, followed by Nymphaea rubra and Cannabis sativa each with RUV 0.83. There were 10 species (e.g., Nelumbo nucifera, Tamarindus indica, Spondias pinnata, Typha domingensis, etc.) with a moderately high RUV of 0.67 (Table 3B). Around 33 species (e.g., Boehmeria glomerulifera, Ficus hispida, Urtica parviflora, several Allium species) demonstrated a RUV of 0.5 (data not shown).
Table 3B
| Species | Number of edible parts | RUV |
|---|---|---|
| Nymphaea nouchali Burm.f. | 6 | 1 |
| Nymphaea rubra Roxb. ex Andrews | 5 | 0.83 |
| Cannabis sativa L. | 5 | 0.83 |
| Nelumbo nucifera Gaertn. | 4 | 0.67 |
| Tamarindus indica L. | 4 | 0.67 |
| Justicia adhatoda L. | 4 | 0.67 |
| Spondias pinnata (L. f.) Kurz | 4 | 0.67 |
| Ensete superbum (Roxb.) Cheesman | 4 | 0.67 |
| Typha domingensis Pers. | 4 | 0.67 |
| Bauhinia variegata L. | 4 | 0.67 |
| Aesculus indica (Wall. ex Cambess.) Hook. | 4 | 0.67 |
| Phyllanthus emblica L. | 4 | 0.67 |
A list of species with multiple edible parts and RUV value (between 0.67 and 1).
Ranking based on CPP value uncovered a list of edible plant parts which are widely consumed, and its value ranged from zero to one (Tables 4A,B). Since the index quantified the acceptability of a plant part among consumers and scored it accordingly, it thereby segregated species in terms of their most valued plant part(s). A few examples of this are: seeds of Cajanus scarabaeoides (0.44), Cannabis sativa (0.33), Euryale ferox (0.357), Nelumbo nucifera (0.218); leaves and shoots of Amaranthus spinosus (0.97), Centella asiatica (0.85), Oxalis corniculata (0.8), Ipomoea aquatica (0.95); flowers of Bauhinia variegata (0.625), Typha domingensis (0.362), Moringa concanensis (0.285); fruits of Ficus racemosa (0.91), Ziziphus jujuba (0.846), Spondias pinnata (0.727), and underground parts of Dioscorea bulbifera (0.896), Dioscorea pentaphylla (0.889), Asparagus racemosus (0.77), etc.
Table 4A
| Species | Total number of citations of all parts | CPP(se) | CPP(l-sh) | CPP(fl) | CPP(fr) | CPP(u) |
|---|---|---|---|---|---|---|
| Oxalis corniculata | 41 | 0.024 | 0.804 | 0.024 | 0.121 | 0 |
| Amaranthus spinosus | 35 | 0 | 0.971 | 0 | 0 | 0 |
| Phyllanthus emblica | 33 | 0.03 | 0.061 | 0.879 | 0 | 0 |
| Colocasia esculenta | 53 | 0 | 0.377 | 0.113 | 0 | 0.433 |
| Solanum americanum | 39 | 0 | 0.487 | 0 | 0.513 | 0 |
| Centella asiatica | 34 | 0 | 0.853 | 0 | 0 | 0 |
| Amaranthus viridis | 30 | 0.067 | 0.933 | 0 | 0 | 0 |
| Chenopodium album | 30 | 0.067 | 0.933 | 0 | 0 | 0 |
| Dioscorea bulbifera | 29 | 0 | 0.034 | 0 | 0.034 | 0.896 |
| Commelina benghalensis | 27 | 0 | 0.852 | 0 | 0 | 0.111 |
| Alternanthera sessilis | 26 | 0 | 1 | 0 | 0 | 0 |
| Dioscorea pentaphylla | 27 | 0 | 0 | 0.074 | 0 | 0.889 |
| Ziziphus jujuba | 26 | 0.038 | 0.115 | 0 | 0.846 | 0 |
| Portulaca oleracea | 22 | 0 | 0.909 | 0 | 0 | 0 |
| Senna tora | 23 | 0.086 | 0.826 | 0.043 | 0.043 | 0 |
| Boerhavia diffusa | 24 | 0 | 0.792 | 0 | 0.042 | 0.083 |
| Ipomoea aquatica | 23 | 0 | 0.957 | 0 | 0.043 | 0 |
| Ficus racemosa | 23 | 0 | 0 | 0 | 0.913 | 0.043 |
| Tamarindus indica | 33 | 0.152 | 0.242 | 0.091 | 0.515 | 0 |
| Asparagus racemosus | 22 | 0 | 0.091 | 0.091 | 0.045 | 0.773 |
| Aegle marmelos | 22 | 0 | 0.091 | 0 | 0.091 | 0 |
| Diplazium esculentum | 20 | 0 | 1 | 0 | 0 | 0 |
| Solanum torvum | 20 | 0 | 0.05 | 0 | 0.95 | 0 |
| Moringa oleifera | 30 | 0.033 | 0.4 | 0.233 | 0.333 | 0 |
| Spondias pinnata | 22 | 0.045 | 0.091 | 0.091 | 0.727 | 0 |
CPP value for selected plants with highest RFC value.
Table 4B
| Species | Total number of citation of all parts | CPP(se) | CPP(l-sh) | CPP(fl) | CPP(fr) | CPP(u) |
|---|---|---|---|---|---|---|
| Colocasia esculenta | 53 | 0 | 0.377 | 0.113 | 0 | 0.434 |
| Phyllanthus emblica | 33 | 0.030 | 0.061 | 0 | 0.879 | 0 |
| Tamarindus indica | 33 | 0.152 | 0.242 | 0.091 | 0.515 | 0 |
| Nelumbo nucifera | 32 | 0.218 | 0.156 | 0.187 | 0 | 0.406 |
| Moringa oleifera | 30 | 0.033 | 0.4 | 0.233 | 0.333 | 0 |
| Nymphaea nouchali | 25 | 0.12 | 0.16 | 0.2 | 0.12 | 0.24 |
| Spondias pinnata | 21 | 0.048 | 0.095 | 0.095 | 0.762 | 0 |
| Bauhinia variegata | 16 | 0 | 0.25 | 0.625 | 0 | 0.0625 |
| Euryale ferox | 14 | 0.357 | 0.357 | 0 | 0.142 | 0.071 |
| Ensete superbum | 13 | 0.077 | 0.308 | 0.231 | 0.307 | 0 |
| Ficus hispida | 13 | 0 | 0.153 | 0.077 | 1 | 0 |
| Dendrocalamus strictus | 12 | 0.167 | 0.583 | 0.083 | 0 | 0.167 |
| Typha domingensis | 11 | 0.091 | 0.272 | 0.362 | 0 | 0.273 |
| Rotheca serrata | 11 | 0 | 0.455 | 0.273 | 0.091 | 0.182 |
| Solena amplexicaulis | 11 | 0 | 0.182 | 0 | 0.545 | 0.273 |
| Justicia adhatoda | 10 | 0 | 0.5 | 0.3 | 0.1 | 0.1 |
| Cannabis sativa | 9 | 0.333 | 0.333 | 0.111 | 0.111 | 0 |
| Cajanus scarabaeoides | 9 | 0.444 | 0.222 | 0 | 0.222 | 0.111 |
| Alpinia galanga | 9 | 0.11 | 0 | 0.22 | 0 | 0.67 |
| Nymphaea rubra | 8 | 0.25 | 0.125 | 0 | 0.25 | 0.25 |
| Borassus flabellifer | 8 | 0.125 | 0.125 | 0.125 | 0.625 | 0 |
| Moringa concanensis | 7 | 0 | 0.428 | 0.285 | 0.285 | 0 |
| Holostemma ada-kodien | 6 | 0 | 0.333 | 0.167 | 0.167 | 0.333 |
| Dregea volubilis | 6 | 0 | 0.333 | 0.167 | 0.5 | 0 |
| Fagopyrum acutatum | 6 | 0.167 | 0.667 | 0 | 0 | 0.167 |
| Allium humile | 5 | 0 | 0.6 | 0.2 | 0 | 0.2 |
| Taraxacum campylodes | 5 | 0 | 0.4 | 0.2 | 0 | 0.2 |
| Flemingia procumbens | 5 | 0 | 0.2 | 0 | 0.2 | 0.6 |
| Aesculus indica | 5 | 0.2 | 0 | 0 | 0.4 | 0.2 |
| Leea asiatica | 5 | 0 | 0 | 0.4 | 0.4 | 0.2 |
| Abutilon indicum | 5 | 0.2 | 0.4 | 0.2 | 0 | 0.2 |
| Malva verticillata | 5 | 0.2 | 0.6 | 0 | 0 | 0.2 |
| Murraya paniculata | 4 | 0 | 0.25 | 0.25 | 0.5 | 0 |
| Boehmeria glomerulifera | 3 | 0 | 0.333 | 0.333 | 0.333 | 0 |
| Urtica parviflora | 3 | 0 | 0.333 | 0.333 | 0 | 0.333 |
| Allium carolinianum | 3 | 0 | 0.333 | 0.333 | 0 | 0.333 |
| Allium jacquemontii | 3 | 0 | 0.333 | 0.333 | 0 | 0.333 |
| Allium tuberosum | 3 | 0 | 0.333 | 0.333 | 0 | 0.333 |
| Trichosanthes tricuspidata | 3 | 0.333 | 0.333 | 0 | 0 | 0.333 |
| Fagopyrum acutatum | 3 | 0.333 | 0.333 | 0 | 0 | 0.333 |
CPP value for selected plants with RUV value between 0.5 and 1.
[CPP(se) - CPP value for seeds, CPP(l-sh) - CPP value for leafy shoots, CPP(fl) - CPP value for flower, CPP(fr) - CPP value for fruits, CPP(u) - CPP value for underground parts].
Prioritization
We shortlisted a set of species for prioritization based on RFC and RUV values (Table 5) in the following manner: (i) highest priority species: it included species which populated both lists, one with a top 25 species scoring 50% of the RFC value (0.213) and the other with an RUV (0.5). fFour species, s Tamarindus indica, Phyllanthus emblica, Colocasia esculenta, and Spondias pinnata, were on the list; (ii) high priority: The rest of the 20 species were in the top 24 species that scored 50% of the RFC value (0.213) or above, e.g., Oxalis corniculata, Amaranthus spinosus, Centella asiatica, Ziziphus jujuba, Solanum americanum, Amaranthus viridis, Commelina benghalensis, Dioscorea pentaphylla, etc; (iii) medium to high priority: a set of nine species with four or more edible parts based on an RUV value between 1 and 0.67 were enlisted, such as Nelumbo nucifera, Nymphaea rubra, N. nouchali, Justicia adhatoda, Cannabis sativa, etc. Relying on the above information, we selected a set of 32 species based on RFC and RUV values for prioritization. This collection of species has been widely used as food sources throughout the country, even in disjunct geographic regions, implying greater acceptance among communities.
Table 5
| Highest priority species | High priority species | Medium to high priority species |
|---|---|---|
| Colocasia esculenta (L.) Schott | Aegle marmelos (L.) Corrêa | Aesculus indica (Wall. ex Cambess.) Hook. |
| Phyllanthus emblica L. | Alternanthera sessilis (L.) R.Br. ex DC. | Bauhinia variegata L. |
| Spondias pinnata (L. f.) Kurz | Amaranthus spinosus L. | Cannabis sativa L. |
| Tamarindus indica L. | Amaranthus viridis L. | Ensete superbum (Roxb.) Cheesman |
| Asparagus racemosus Willd. | Justicia adhatoda L. | |
| Boerhavia diffusa L. | Nelumbo nucifera Gaertn. | |
| Centella asiatica (L.) Urb. | Nymphaea nouchali Burm.f. | |
| Chenopodium album L. | Nymphaea rubra Roxb. ex Andrews | |
| Commelina benghalensis L. | Typha domingensis Pers. | |
| Dioscorea bulbifera L. | ||
| Dioscorea pentaphylla L. | ||
| Diplazium esculentum (Retz.) Sw. | ||
| Ficus racemosa L. | ||
| Ipomoea aquatica Forssk. | ||
| Oxalis corniculata L. | ||
| Portulaca oleracea L. | ||
| Senna tora (L.) Roxb. | ||
| Solanum americanum Mill. | ||
| Solanum torvum Sw. | ||
| Ziziphus jujuba Mill. |
A list prioritized species based on RFC and RUV values.
Discussion
A culture of WEP collection from nearby forested patches, fringes of agricultural fields, or from the homestead has been ubiquitous in developing and many developed countries. It constituted a healthy and sustainable food system widely documented across the globe (Scoones et al., 1992; Mazhar et al., 2007; Bharucha and Pretty, 2010; Rowland et al., 2016). Determining the popularity of such an exercise within India revealed a remarkable diversity of wild flora in regular use. Of which, many of these have been used across widely divergent cultural geographic regions or have multiple useful edible organs. In addition, being a standard component of daily diet, the contribution of wild food to food uncertainty, shortages, and agricultural regression has widely been acknowledged (Ertug, 2014). It suggests the habit of eating wild plants falls in the larger domain of human environment interactions and has evolved over many generations to help manage natural resources.
Taxonomic Diversity
A series of regional studies have uncovered the great wealth of wild flora being used as food that has not entered into mainstream cultivation (Singh and Arora, 1978; Sinha and Lakra, 2005; Angami et al., 2006; Jeyaprakash et al., 2011). Similarly, the diverse spectra of edible plant species (1403 species) belonging to nearly 200 families reflect that it has been a deep-rooted practice in India. Inclusion of a wide variety of plants of different habits, growth forms, and usable organs in the dietary repertoire also underscores their acceptance and assimilation into food culture. The breadth of plant use is high compared to the other countries or regions (such as Southeast Asia or the Mediterranean), which seems plausible given the enormous size of the country and its inherent bio-cultural diversity (Loh and Harmon, 2005; Maffi and Woodley, 2012). The choice of food or medicinal species is often governed by many factors, where plant availability is a primary driver. Plant availability and distribution are largely determined by environmental parameters, e.g., soil type, temperature, altitude, rainfall, etc., that significantly affect the peoples' choices (Turner et al., 2011; Chevalier et al., 2014b). India covers a large geographic expanse with a high floral diversity, which harbors many biogeographic zones and hotspots that shelter a wide diversity of plants (Nayar, 1996). In addition, the high bio-cultural diversity has resulted in the divergent human adaptation to manage and use an enormous variety of plant resources in a dynamic manner (Berkes, 2009; Maffi and Woodley, 2012; Chevalier et al., 2014b). This fact is also reflected in the array of WEP species regularly consumed by people.
Although a rich collection of WEP is in the spectrum of food choice, we uncovered a preponderance of a handful of families (forty-four families make up about 75% of the total species count). Human preference for a narrow subset from a large pool of floral families is a common trend that has been previously observed in medicinal plant use, and researchers strove to explain the underlying reason (Moerman, 1996; Leonti et al., 2003). The same trend of over- and under-use has also been noted in wild edibles, though not explicitly stated (Turner et al., 2011). The predominance of Leguminosae (8%) has been reported from elsewhere in Southeast Asia; likewise, the top ten speciose families shown in our results, such as Poaceae, Rosaceae, Moraceae, Lamiaceae, Compositae, Araceae, etc., have also been reported from studies carried out in Southeast Asia (Cruz-Garcia and Price, 2011; Sujarwo et al., 2014; Shin et al., 2018). On the other hand, the peoples' choices in European countries remained with Rosaceae, Liliaceae, Lamiaceae, Asteraceae, and Apiaceae members, whereas there was a visible absence of Poaceae, Moraceae, Amaranthaceae, Malvaceae, and a minimal presence of Leguminosae (Leonti et al., 2006; Tardío et al., 2006; Pardo-de-Santayana et al., 2007; Hadjichambis et al., 2008; González et al., 2011; Dogan et al., 2013). The underlying reason of the sharing of edible flora could be due to a strong biogeographic affinity between South and Southeast Asia, where the Indo-Malayan biota represented a major fraction (Mani, 1974). A study carried out in South Africa by Ogle and Grivetti (1985a) revealed a prevalence of selected families, such as Compositae, Myrtaceae, Moraceae, Rubiaceae, Leguminosae, and Amaranthaceae that broadly overlap with Asian assemblage.
Likewise, a strong bias in choosing certain species has also been observed. It seems that some species were more overly used than others, a fact which was reflected in their RFC value spectrum. The index also signified an apparent importance of the species in terms of its frequency of use (i.e., how many times it has been cited considering all the studies?) and the degree of its acceptance among various communities (i.e., what is the spatial limit of its use?). For example, Alternanthera sessilis, a high-rank species with a magnitude of RFC 0.29, is a plant which has been widely used from southern to north-eastern through eastern India. Likewise, there were many members which demonstrated a similarly wider acceptance, e.g., Oxalis corniculata, Amaranthus spinosus, Centella asiatica, etc. Throughout literature, the choice of certain taxa has widely been reported from studies on Asia, Europe, and Africa; only the preferred set of species varied with geography (Ogle and Grivetti, 1985a,b; Tardío et al., 2006; Hadjichambis et al., 2008; Cruz-Garcia and Price, 2011; Sujarwo et al., 2014). The underlying drivers of peoples' choices could be multiple, e.g., abundance, easy accessibility, taste, prior knowledge or experience, etc. (Chevalier et al., 2014b; Albuquerque et al., 2015). On the other hand, there were also instances where commonly available species had a narrow use in culinary practices, perhaps due to lack of information, or cultural inclination. Examples can be drawn from Tephrosia purpurea, Albizia odoratissima, Leucas stricta, and Gmelina arborea which are locally relished (RFC 0.011 for each).
Use by Parts
Plant/people interactions have been the backbone of human evolution, since all cultures have to subsist on plant resources (Cruz-Garcia and Ertug, 2014). Humans have employed a diverse collection of floral parts in their diets for a long time, e.g., fleshy leafy shoots, underground starch-rich parts, ripe and unripe fruits, flowers, and seeds. Additionally, many other parts are also regularly consumed, such as pith, bark, arils, peduncles, bulbils, latex, etc. Of these, prehistory is replete with examples of the harvest of various roots and tubers to derive starchy food (Ezell et al., 2006). Other examples, such as the charred remains of seeds or grains, were also often uncovered in archeological specimens (Harris and Hillman, 2014; Melamed et al., 2016); absent were the leaves or tender shoots or flowers. Altogether, the range highlights divergent human choice and their post-harvest processing that had established its roots from the hunting-gathering phase (Chevalier et al., 2014a,b).
In our study, the grouping of WEP based on edible parts has offered a deeper understanding of the underlying trend of use, i.e., how edible parts drive plant use, which parts are being eaten the most, etc. From total used species, it was revealed that most have been used as leafy greens (52.7%) and fruits (47.6%), followed by underground parts (15.7%), seeds (12.8%), and flowers (11.2%). Turner et al. (2011) underscored the preference toward the specific type of wild edible consumption and attributed it to prevailing climatic condition in an ecosystem that perhaps determines peoples' choice. They also highlighted the role of culture in shaping the type of wild edible use, such as the frequent use of leafy greens in east and south Asia being in vogue. In a study conducted by Cruz-Garcia and Price (2011), the highest edible species clustered in the “shoot” and “fruit” category; however, their grouping does not entirely match with the part-wise classification we implemented. Similar leaning on wild leafy green use has also been reported by Sujarwo et al. (2014) in Bali. The inclination toward leafy greens is a common observation across the east Asian countries, such as Korea (Pemberton and Lee, 1996), Thailand (Price, 2006), Vietnam (Ogle, 2001), and China (Hu, 2005) and is often termed as herbophilia (Luczaj, 2008) to refer to peoples' liking of leafy greens. It is in sharp contrast with northern Europe where wild vegetables have been used very little (Luczaj, 2008), or in the Amazon where they are hardly used at all (Katz et al., 2012).
When the edible species pool is broken into six categories of the basis of parts, Leguminosae outnumbered other families in most of the categories, i.e., seeds, flowers, and shoots. It is also the second largest family in the fruit category and the fourth largest in underground parts. One underlying reason could be the unprecedented species diversity of Leguminosae in the tropics. The predominance of Leguminosae members has also been a common finding in several similar studies from the southeast Asian countries where it contributes significantly to the floral diversity (Cruz-Garcia and Price, 2011). Likewise in the fruit category, an abundance of Rosaceous species could be a reflection of the overall high use breadth of Rosaceae members, as reported from Mediterranean or European countries (Tardío et al., 2006; Luczaj, 2012). Rosaceae is an important family which generally shares major floral elements that have been formally cultivated for fruits. In the root and tuber category, members of Dioscoreaceae, Araceae, Zingiberaecae, and Amaryllidaceae outnumbered others, which is also in concord with other studies (Turner et al., 2011).
Evaluation of species' importance in terms of their multiple palatable plant parts made use of the index, RUV, that selected and ranked edible species based on the number of useful parts. Likewise, an inclusion of CPP value added a reliability measure to the various edible parts of species selected for prioritization. Collectively, the indices (RFC and RUV) allowed an informed decision on shortlisting species based on the analyses of the collected data.
Prioritization—Inclusion in Policy for Nutritional Security
Assimilation of wild edible plants into the diet has much larger implications in terms of environmental sustainability, when the world is plagued with the grave crises of climate change and food insecurity, and could lessen the footprints of agriculture and allow for a shift toward more sustainable food systems. Judicious use of intrinsic resources with less negative impact has become critical and adoption of WEP resources could emerge as a sustainable strategy (Bharucha and Pretty, 2010). Wild food offers several advantages on this line, i.e., wide diversity, easy access to the local resource base, availability, time-tested reliability, little or no management, etc. (Mazhar et al., 2007; Bharucha and Pretty, 2010; Cruz-Garcia and Price, 2011; Turner et al., 2011). Moreover, the problem of micronutrient deficiency or “hidden hunger” that looms large over the global population cannot be erased by staple crops which lack essential micronutrients (Guralnik et al., 2004; Pingali, 2015; Ickowitz et al., 2019). Yet fortification of commercial food and production of bio-fortified food crops bred with increased micronutrient content have also been proposed to combat hidden hunger. Here, the untapped nutritional potential of wild food to enhance dietary diversity and nutritional outcome has a central role to play (Table 6). They are reservoirs of many vitamins andtrace elements, e.g., leafy shoots (e.g., Boerhaavia diffusa, Aerva lanata) are a source of vitamin A and Calcium, fruits (Tamarindus indica), are a source of iron and zinc, etc. Their health benefits have also been widely reported from various countries with a tradition of eating wild edibles (Ogle and Grivetti, 1985a,b; Cook et al., 2000; Ogle, 2001; Ogle et al., 2003; Simopoulos, 2004; Uusiku et al., 2010; Ranfa et al., 2014; Mishra et al., 2015; Hama-Ba et al., 2017). A couple of studies examining selected edible plants from various parts of India (such as Sikkim, Jharkhand, the north-eastern region, and South India) also supports the same fact (Rajyalakshmi et al., 2001; Sundriyal and Sundriyal, 2001; Bhatt et al., 2005; Ghosh-Jerath et al., 2015). In sum, positive health implications of wild edibles have long been acknowledged either formally through research or informally through age-long traditional wisdom. Nevertheless, owing to several entangled factors, the practice is currently at stake.
Table 6
| Edible species | Parts | Vit A | Vit B1 | Vit B2 | Vit C | Vit E | Ca | Fe | Zn | Na | K | Cu | P | Mg | Mn | Se | Folic acid |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Aegle marmelos | Fr | 186 | 0.01 | 1.2 | X | X | 85 | 0.6 | X | X | 0.6 | X | 31.8 | X | X | X | X |
| Aerva lanata | L, Sh | 21.76 | X | X | 19 | X | 322 | 22.06 | 0.65 | 10.4 | X | X | X | X | X | X | 0.04 |
| Aesculus indica | Se | X | X | X | X | X | 8.20 | 8.50 | 705.9 | X | 81.00 | 0.6 | X | X | 0.5 | X | X |
| Agaricus sp. (Chiple) | Fruit body | X | X | X | X | X | 1.842 | 0.13 | 0.73 | 0.053 | 1.92 | 0.07 | 0.47 | 0.23 | X | X | X |
| Agaricus sp. (Patpate) | Fruit body | X | X | X | X | X | 1.53 | 0.11 | 0.6 | 0.06 | 2.17 | 0.09 | 0.76 | 0.34 | X | X | X |
| Alternanthera sessilis | L, Sh | 1.92 | 0 | 0.14 | 17 | X | 510 | 1.63 | X | X | X | X | X | X | X | X | X |
| Amaranthus spinosus | L, Sh | 3.56 | 0 | X | 33 | X | 800 | 22.9 | X | X | X | X | X | X | X | X | X |
| Amaranthus tricolor | L, Sh | 5.52 | 0.03 | 0.3 | 99 | X | 397 | 3.49 | 0.18 | 230 | X | X | X | X | X | X | 0.14 |
| Amaranthus viridis | L, Sh | X | X | X | 179 | X | 330 | 18.7 | X | X | X | X | X | X | X | X | X |
| Antidesma acidum | L, Sh | X | X | X | X | X | 1717 | X | X | X | X | X | X | X | X | X | X |
| Aralia leschenaultii | Fr | X | X | X | X | X | 0.31 | 0.6 | X | 0.6 | 1.89 | X | 0.47 | 0.25 | X | X | X |
| Ardisia macrocarpa | Fr | X | X | X | X | X | 0.29 | 0.02 | 0.31 | 0.04 | 0.89 | 0.07 | 0.13 | 0.31 | X | X | X |
| Arisaema utile | Fr | X | X | X | X | X | 0.92 | 0.83 | X | 0.09 | 2.4 | X | 0.69 | 0.62 | X | X | X |
| Artocarpus lakoocha | Fr | 0.25 | 0.02 | 0.15 | 135 | X | 50 | 0.05 | X | X | X | X | X | X | X | X | X |
| Baccaurea ramiflora | Fr | X | X | X | 0.27 | X | 0.16 | 0.08 | 0.6 | 0.04 | 0.73 | 0.08 | 0.13 | 0.5 | X | X | X |
| Bambusa bambos | L, Sh | 0 | 0.08 | 0.19 | 5 | X | 20 | 0.1 | X | X | X | X | X | X | X | X | X |
| Bambusa tulda | L, Sh | X | X | X | 1.42 | 0.61 | 4.06 | 3.19 | 0.72 | 19.96 | 408 | 0.44 | X | X | X | X | X |
| Bauhinia purpurea | L, Sh | X | X | X | X | X | 312 | X | X | X | X | X | X | X | X | X | X |
| Boerhaavia diffusa | L, Sh | 16.01 | X | X | 12 | X | 202 | 10.68 | 0.41 | 39.4 | X | X | X | X | X | X | 0.02 |
| Cannabis sativa | L, Sh | X | 0.4 | 0.1 | X | 90 | 145 | 14 | 7 | 12 | 859 | 2 | X | 483 | 7 | X | X |
| Carissa carandas | Fr | X | X | X | X | X | 21 | X | X | X | X | X | X | X | X | X | X |
| Castanopsis indica | Fr | X | X | X | X | X | 1540 | 2.6 | 1.53 | 0.03 | 4.33 | 0.77 | 80 | 12.68 | 2.35 | 0.0006 | X |
| Celosia argentea | L, Sh | X | X | X | X | X | 323 | X | X | X | X | X | X | X | X | X | X |
| Centella asiatica | L, Sh | 0.5 | 0.53 | X | 5 | X | 231 | 55.66 | 1.92 | 5.2 | X | X | X | X | X | X | 0.01 |
| Chenopodium album | L, Sh | 1.74 | 0.01 | 0.14 | 35 | X | 150 | 4.2 | X | X | X | X | X | X | X | X | X |
| Choerospondias axillaris | Fr | X | X | X | 0.04 | X | 1.58 | 0.11 | 0.83 | 0.04 | 0.67 | 0.06 | 0.16 | 0.68 | X | X | X |
| Colocasia antiquorum | L, Sh | 5.92 | 0.22 | 0.26 | 12 | X | 227 | 10 | X | X | X | X | X | X | X | X | X |
| Colocasis esculenta | U | X | X | X | X | X | 19 | 1.1 | 1.7 | 1 | 340 | X | X | 28 | X | X | X |
| Commelina benghalensis | L, Sh | X | X | X | X | X | 1431.6 ±ramya 6.41 | 115.92 ±ramya 5.51 | 2.68 ±ramya 0.17 | 200 ±ramya 7.02 | 390 ±ramya 15.52 | 2.72 ±ramya 0.09 | X | 220.8 ±ramya 4.15 | 7.98 ±ramya 0.26 | X | X |
| Crotalaria juncea | L, Sh | X | X | X | X | X | 200 | X | X | X | X | X | X | X | X | X | X |
| Dendrocalamus strictus | L, Sh | X | X | X | 2.43 | 0.58 | 139.5 | 2.91 | X | 0.08 | X | X | 58.13 | 0.17 | X | X | X |
| Dioscorea bulbifera | U | 0.3 | X | X | 4 | X | 20 | 4.09 | 0.38 | 0.08 | X | X | X | X | X | X | 0.028 |
| Diospyros melanoxylon | Fr | 0.361 | 0.01 | 0.04 | 1 | X | 60 | 0.5 | X | X | X | X | X | X | X | X | X |
| Diplazium esculentum | Fr | X | X | X | X | X | 1.02 | 0.56 | 0.58 | 0.08 | 2.37 | 0.04 | 0.5 | 0.51 | X | X | X |
| Diploknema butyracea | Fr | X | X | X | 0.03 | X | 0.82 | 0.18 | 0.86 | 0.07 | 0.82 | 0.04 | 0.09 | 0.61 | X | X | X |
| Elaeagnus latifolia | Fr | X | X | X | 0.07 | X | 1.47 | 0.18 | 1.19 | 0.05 | 0.91 | 0.05 | 0.09 | 0.54 | X | X | X |
| Elaeagnus rhamnoides | Fr | X | X | X | 0.26 | X | 0.17 | 0.06 | 0.88 | X | X | 0.02 | 0.31 | 0.31 | X | X | X |
| Elaeocarpus sikkimensis | Fr | X | X | X | 0.01 | X | 0.63 | 0.15 | 0.64 | 0.04 | 1.01 | 0.08 | 0.07 | 0.35 | X | X | X |
| Ensete superbum | Fl | X | X | X | X | X | 665.6 ±ramya 5.94 | 518.4 ±ramya 11.06 | 3.78 ±ramya 0.15 | 600 ±ramya 4.58 | 180 ±ramya 6.11 | 4.46 ±ramya 0.15 | X | 176.8 ±ramya 4.86 | 11.74 ±ramya 0.46 | X | X |
| Enydra fluctuans | L, Sh | 0.98 | 0.96 | X | 4 | X | 246 | 16.99 | 0.94 | 80 | X | X | X | X | X | X | 0.096 |
| Euphorbia granulata | L, Sh | 11.68 | 3.07 | X | 9 | X | 425 | 81.09 | 1.01 | 24.9 | X | X | X | X | X | X | 0.072 |
| Ficus bengalenis | Fr | X | X | X | X | X | 364 | X | X | X | X | X | X | X | X | X | X |
| Ficus geniculata | L, Sh | 0.53 | X | X | 5 | X | 672 | 8.89 | 4.63 | 11.3 | X | X | X | X | X | X | 0.012 |
| Ficus racemosa | Bark | X | X | X | X | X | 172.9 | 15.92 | 0.05 | 25.5 | 1197.5 | 0.52 | X | 19.62 | 0.19 | X | X |
| Ficus sp. | L, Sh | 8.2 | X | X | X | X | 295 | 2.77 | 0.8 | 7.5 | X | X | X | X | X | X | 0.039 |
| Hibiscus cannabinus | L, Sh | 6.97 | 0.07 | 0.39 | 20 | X | 172 | 2.28 | 0.27 | X | X | X | X | X | X | X | X |
| Ipomoea aquatica | L, Sh | 1.98 | 0.05 | 0.13 | 37 | X | 110 | 3.9 | X | X | X | X | X | X | X | X | X |
| Kaempferia galanga | U | X | X | X | X | X | 950 | 69.91 | 8.35 | 0.32 | 12.23 | 0.91 | 60 | 293.92 | 42.65 | 0.0012 | X |
| Leucas cephalotes | L, Sh | 18.46 | X | X | 8 | X | 236 | 20.02 | 0.8 | 10.6 | X | X | X | X | X | X | 0.01 |
| Madhuca neriifolia | Fr | 0.307 | X | X | 40 | X | 45 | 0.23 | X | X | X | X | X | X | X | X | X |
| Marsilea minuta | L, Sh | X | X | X | X | X | 53 | X | X | X | X | X | X | X | X | X | X |
| Meyna spinosa | L, Sh | X | X | X | X | X | 127 | X | X | X | X | X | X | X | X | X | X |
| Moringa oleifera | L, Sh | 6.78 | 0.06 | 0.05 | 220 | X | 440 | 0.85 | 0.16 | X | X | X | X | X | X | X | X |
| Moringa oleifera | Fr | X | X | X | X | X | 51 | X | X | X | X | X | X | X | X | X | X |
| Nelumbo nucifera | Se | X | 0.22 | 0.01 | 3.94 | 0.46 | 44.5 | 1.3 | 1.3 | 3.3 | 1630 | 1 | X | 165 | 5.7 | X | X |
| Nymphaea nouchali | L, Sh | X | X | X | X | X | 379.54 ±ramya 0.58 | 3.59 ±ramya 0.09 | 3.63 ±ramya 0.13 | 643.58 ±ramya 0.82 | 858.39 ±ramya 0.68 | 1.77 ±ramya 0.11 | X | 145.48 ±ramya 1.11 | X | X | X |
| Nymphaea rubra | U | X | X | X | 14.43 ±ramya 0.03 | X | 354.1 ±ramya 018 | 28.14 ±ramya 0.24 | 1.64 ±ramya 0.01 | 34.1 ±ramya 0.36 | 734 ±ramya 0.74 | 1.12 ±ramya 0.01 | X | 104 ±ramya 0.06 | 1.34 ±ramya 0.01 | X | X |
| Oxalis corniculata | L, Sh | X | X | X | 21 | X | 234 | 14.75 | X | X | X | X | X | X | X | X | X |
| Phyllanthus emblica | Fr | X | X | X | X | X | 27.6 | 3.3 | 1.8 | 4.2 | 282.0 | 0.28 | 28.2 | 11.8 | 1.1 | 0.24 | X |
| Polygonum molle | Fr | X | X | X | X | X | 0.15 | 0.32 | 0.28 | 0.09 | 2.02 | 0.06 | 0.27 | 0.43 | X | X | X |
| Polygonum plebeium | L, Sh | X | X | X | X | X | 194 | X | X | X | X | X | X | X | X | X | X |
| Portulaca oleracea | L, Sh | X | X | X | 15 | X | 227 | 16.17 | X | X | X | X | X | X | X | X | X |
| Prunus cerasoides | Fr | X | X | X | 0.32 | X | 0.2 | 0.21 | 0.2 | 0.02 | 0.47 | 0.01 | 0.18 | 0.59 | X | X | X |
| Prunus napaulensis | Fr | X | X | X | 608.9 | X | 1220 | 10.7 | 1.49 | 0.1 | 16.5 | 1.22 | 70 | 217.74 | 6.62 | 0.0005 | X |
| Quercus robur | Fr | X | X | X | X | X | 410 | 4.7 | 1.59 | 0.13 | 8.3 | 1.66 | 150 | 126 | 5.63 | 0.0002 | X |
| Rhus chinensis | Fr | X | X | X | X | X | 1020 | 4.17 | 2.37 | 0.03 | 8.41 | 0.63 | 160 | 111.1 | X | 0.0009 | X |
| Schleichera trijuga | Fr | X | X | X | X | X | 15 | X | X | X | X | X | X | X | X | X | X |
| Semecarpus anacardium | Fr | X | X | X | X | X | 295 | 6.1 | X | X | X | X | X | X | X | X | X |
| Senna tora | L, Sh | 10.512 | 0.08 | 0.19 | 82 | X | 520 | 12.4 | X | X | X | X | X | X | X | X | X |
| Solanum torvum | L, Sh | 0.078 | X | X | 2.686 | X | 22.15 | 7.68 | 2.14 | X | X | 0.26 | X | X | 1.95 | X | X |
| Spondia pinnata | Fr | X | X | X | X | X | 0.93 | 1.32 ±ramya 0.02 | X | 1.54 ±ramya 0.01 | 1.38 ±ramya 0.80 | 1.23 ±ramya 0.03 | 0.68 ±ramya 0.01 | X | X | X | X |
| Tamarindus indica | Fr | X | X | X | X | X | 248.56 ±ramya 1.3 | 7.14 ±ramya 0.92 | 6.94 ±ramya 0.51 | 28.83 ±ramya 1.34 | 1315.28 ±ramya 5.74 | 0.59 ±ramya 0.16 | 369.47 ±ramya 2.14 | 285.14 ±ramya 2.82 | 0.81 ±ramya 0.12 | X | X |
| Terminalia chebula | Fr | X | X | X | X | X | 0.81 | 0.03 | 0.44 | 0.08 | 1.27 | 0.04 | 0.04 | 0.3 | X | X | X |
| Trianthema portulacastrum | L, Sh | X | X | X | 70 | X | 100 | 38.5 | X | X | X | X | X | X | X | X | X |
| Urtica dioica | Fr | X | X | X | X | X | 1.31 | 1.31 | X | 0.07 | 1.87 | X | 0.27 | 0.42 | X | X | X |
| Viburnum corylifolium | Fr | X | X | X | 238.7 | X | 630 | 3.55 | 1.62 | 0.11 | 11.13 | 1.27 | 140 | 161.39 | 9.63 | 0.0002 | X |
| Vicia hirsuta | L, Sh | 0.55 | X | X | 23 | X | 215 | 7.78 | 4.11 | 33.18 | X | X | X | X | X | X | 0.07 |
| Zanthoxylum rhetusa | Fr | X | X | X | X | X | 0.88 | 0.05 | 1.16 | 0.02 | 0.72 | 0.12 | 0.14 | 0.35 | X | X | X |
| Ziziphus jujuba | Fr | 0.21 | 0.02 | 0.05 | 76 | X | 4 | 0.5 | 0.1 | X | X | X | X | X | X | X | X |
Nutritional composition of a few selected wild edible plants (in mg/100 g).
Vit A, Vitamin A; Vit B1, Vitamin B1; Vit C, Vitamin C; Ca, Calcium; Fe, Iron; Zn, Zinc; Na, Sodium; K, Potassium; Mg, Magnesium; Mn, Manganese; Se- Selenium; Cu, Copper; P, Phosphorous. L; Sh, leafy shoots/ shoots/ leaves; Fr, Fruits; Fl, Flowers; Se, Seeds; U, underground parts; roots/tuber.
(Wills et al., 1983; Barthakur and Arnold, 1991; Callaway, 2004; Pugalenthi et al., 2004; Sheela et al., 2004; Rathore, 2009; Ahmed et al., 2010; Andola and Purohit, 2010; Mohan and Kalidass, 2010; Mahadkar et al., 2012; Akoto et al., 2015; Zhang et al., 2015; Satter et al., 2016; Mishra et al., 2018).
One of the largely agreed reasons is agricultural intensification that has substantially increased the staple crop production, but has significantly reduced farmland biodiversity and dietary diversity (Dewey, 1981; Fowler and Mooney, 1990; Pretty, 1995; Pingali, 2015). It has also brought in an intensive use of agrochemicals that acted in tandem with other factors like land-use change, forest fragmentation, and a change in governance to decimate the wild population of edible plants or their habitat (Pretty, 1995; Bharucha and Pretty, 2010; Padoch and Sunderland, 2014; Broegaard et al., 2017; Ickowitz et al., 2019). Many other cultural factors, e.g., changing food habit, loss of traditional knowledge systems, the overwhelming presence of dominant food culture, and easy access to store food have also acted hand in hand to erode the culture of eating wild food (Luczaj, 2012). The eventual outcome is a loss of dietary diversity and disruption of the sustainable food systems. Here, the lower strata of economic groups of developing countries are worst hit as the malnourishment owing to micronutrient deficiency is acute among rural populations (Von Grebmer et al., 2014). It is because the decline of wild edibles population robbed them of the easily obtainable nutrition and buying the equivalent food items from the market place always incurred an extra cost, thus impairing the access. It is especially imperative for a developing country like India, where a major section of the population cannot afford to buy essential nutrients from nearby markets for various reasons, price being the primary reason, and where the nutritional benefits of local resources in the form of wild edibles in social welfare cannot be undermined.
A potential way out could be the revival of the culture by promoting informal cultivation or moderate management in homesteads, fringes, pastures, or fallow lands (Broegaard et al., 2017). The issue deserves a synergy among research, education and outreach, and policy. For the resumption of such an exercise, a prioritization program would be a better point to commence if bolstered by data-driven inference; here we aim to objectively prioritize a handful of plants that might facilitate policy formulation. Our analyses have selected a small subset from the 1,400 edible species on the basis of their high RFC and RUV values. The indices stand for the easy availability, greater accessibility, and relatively wider acceptance among people residing in distant geographic regions and therefore these attributes justify their inclusion into the prioritization and policy formation. For example, the ubiquity of Oxalis corniculata, Amaranthus spinosus, Solanum americanum, Centella asiatica, Alternanthera sessilis, and Ipomoea aqautica, etc., indicates their easy procuring and cross-cultural assimilation. On the other hand, species such as Nymphaea nouchali, N. rubra, Nelumbo nucifera, Cannabis sativa, Tamarindus indica, Spondias pinnata, and Dregea volubilis also represent a high degree of usability for their use of three or even more parts (Figures 5A–D). Several reports have explicitly highlighted their nutritional benefits in terms of vitamins and minerals (Table 6). So, these prioritized plants deserve the attention of researchers, policymakers, and farmers to be integrated toward a sustainable food system. In the absence of appropriate policy, it could remain localized and may not widely exert its beneficial effect on nutritional security. Moreover, many were already well-assimilated into local or regional food culture, but have been eroded over time, and could be resurrected through a promotion to sensitize consumers and would gain momentum with policy in place.
Figure 5
Conclusion
It has largely been recognized that food security is ensured when all people have access to sufficient and nutritious food (World Food Summit, 1996). Nutritious food relates to dietary quality and diversity that are indicators of an adequate amount of micro-nutrients in the diet (World Health Organization, 2008; Royal Society, 2009; FAO and FHI 360, 2016). Yet strategies for ensuring food security often advocate for an intensified agriculture that focusses on the enhanced production of major cereals only (FAO, 2012; Jones, 2017), but remaining quite blind to dietary diversity, thus disrupting healthy food systems (Pingali, 2015). While there is a consensus that wild uncultivated foods cannot entirely erase the gap between supply and demand, the researchers underscore that the difference between supply and demand would be much wider if wild food was absent from our food system (Bharucha and Pretty, 2010).
Our study uncovered a great majority of WEP from nearly two hundred families has been consumed regularly around India. Various parts, leafy shoots, fruits, flowers, seeds, or underground organs are generally included in the food repertoire. Procured from anthropogenic landscapes, many of these have cross-cultural acceptance and are valued for their specific organ, while many are important for their multi-part usage; they can be prioritized for policy decisions. The diversity of edible flora, their multifarious usage across various cultural geographic regions, and wider mentions, strongly suggest the fact that the practice of eating from the wild has been an age-old exercise. This practice may have eroded over time but could be resurrected with the proper framework, policy, and information dissemination. It is also imperative to shift our focus from a small subset of plants and embrace a diverse food base in order to enrich our dietary quality. Additionally, a diverse resource base would enable our food system to be more resilient in the face of climatic changes.
Statements
Data availability statement
The datasets generated for this study could be available from the corresponding author on request with proper justification and on mutual agreement.
Author contributions
AR and RR designed the study, collected, compiled, and analyzed the data. ES helped in data collection. AR and RR wrote the manuscript with inputs from ES.
Acknowledgments
We acknowledge the informal discussions with Abhra Chakraborty, Rakesh Mitra, and Sumit Sarkar in various stages of the study. We would like to thank Rahul Mukherjee and Karen Meehan for language editing and three reviewers for their suggestions. We received no funding for this study.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fsufs.2020.00056/full#supplementary-material
References
1
Agrahar-MurugkarD.SubbulakshmiG. (2005). Nutritive values of wild edible fruits, berries, nuts, roots and spices consumed by the Khasi tribes of India. Ecol. Food Nutr.44, 207–223. 10.1080/03670240590953025
2
AhmedF.AshaM. R.UroojA.BhatK. K. (2010). Ficus racemosa bark: nutrient composition, physicochemical properties and its utilization as nutra tea. Int. J. Nutr. Metab.2, 033–039.
3
AjeshT. P.NaseefS. A.KumuthakalavalliR. (2012). Ethnobotanical documentation of wild edible fruits used by muthuvan tribes of Idukki, Kerala-India. Int. J. Pharm. BioSci.3, 479–487.
4
AkotoO.BorquayeL. S.HowardA. S.KonwurukN. (2015). Nutritional and mineral composition of the fruits of Solanum torvum from Ghana. Int. J.Chem. Biomol. Sci.1, 222–226.
5
AlbuquerqueU. P.SoldatiG. T.RamosM. A.de MeloJ. G.de MedeirosP. M.NascimentoA. L. B.et al. (2015). The influence of the environment on natural resource use: evidence of apparency, in Evolutionary Ethnobiology, eds AlbuquerqueU.De MedeirosP.CasasA. (Cham: Springer), 131–147. 10.1007/978-3-319-19917-7_10
6
AndersonE. N.PearsallD. M.HunnE. STurnerN. J. (eds.). (2011). Ethnobiology. Hoboken, NJ: John Wiley & Sons, Inc. 10.1002/9781118015872
7
AndolaH. C.PurohitV. K. (2010). Evaluation of nutritive and mineral value in ripe fruits of Spondias pinnata from two location of Western Himalaya, India. Med. Plants2, 233–236. 10.5958/j.0975-4261.2.3.037
8
AngamiA.GajurelP. R.RethyP.SinghB.KalitaS. K. (2006). Status and potential of wild edible plants of Arunachal Pradesh. Indian J. Tradit. Know.5, 541–550
9
AngelsenA.JaggerP.BabigumiraR.BelcherB.HogarthN. J.BauchS.et al. (2014). Environmental income and rural livelihoods: a global-comparative analysis. World Dev.64(Suppl. 1), S12–S28. 10.1016/j.worlddev.2014.03.006
10
ArinathanV.MohanV. R.BrittoA.MuruganC. (2007). Wild edibles used by Palliyars of the western Ghats, Tamil Nadu. Indian J. Tradit. Know.6, 163–168
11
AyyanarM.IgnacimuthuS. (2005). Traditional knowledge of Kani tribals in Kouthalai of Tirunelveli hills, Tamil Nadu, India. J. Ethnopharmacol.102, 246–255. 10.1016/j.jep.2005.06.020
12
BarthakurN. N.ArnoldN. P. (1991). Chemical analysis of the emblic (Phyllanthus emblica L.) and its potential as a food source. Sci. Hortic.47, 99–105. 10.1016/0304-4238(91)90031-S
13
BaruaP. T.TomarR. S. (2014). Role of genus cassia in combating malnutrition in Sahariya dominated Sheopur kalan region of Madhya Pradesh. Int. J. Sci. Res.3, 868–872
14
BediS. J. (1978). Ethnobotany of the Ratan Mahal Hills, Gujarat, India. Econ. Bot.32, 278–284. 10.1007/BF02864701
15
BeheraK. K.MishraN. M.DhalN. K.RoutN. C. (2008). Wild edible plants of Mayurbhanj district, Orissa, India. J.f Econ. Taxon. Bot.32, 305–314.
16
BerkesF. (ed.). (2009). Sacred Ecology: Traditional Ecological Knowledge and Resource Management. 2nd edn. Philadelphia (PA): Taylor and Francis.
17
BharuchaZ.PrettyJ. (2010). The roles and values of wild foods in agricultural systems. Phil. Trans. R. Soc. B.365, 2913–2926. 10.1098/rstb.2010.0123
18
BhattB. P.SinghK.SinghA. (2005). Nutritional values of some commercial edible bamboo species of the North Eastern Himalayan region, India. J. Bamboo Rattan4, 111–124. 10.1163/1569159054699317
19
BinuS. (2010). Wild edible plants used by the tribals in Pathanamthitta district, Kerala. Indian J. Tradit. Know.9, 309–312
20
BiswasK.DasA. P. (2011). Documentation of wild leafy vegetables from the tribal dominated parts of Malda District of Paschimbanga, India, in Recent Studies in Biodiversity and Traditional Knowledge in India eds. GhoshC.DasA. P. (Malda: Gour College), 301–306.
21
BroegaardR. B.RasmussenL. V.DawsonN.MertzO.VongvisoukT.GroganK. (2017). Wild food collection and nutrition under commercial agriculture expansion in agriculture-forest landscapes. For. Policy Econ.84, 92–101. 10.1016/j.forpol.2016.12.012
22
CallawayJ. C. (2004). Hempseed as a nutritional resource: an overview. Euphytica140, 65–72. 10.1007/s10681-004-4811-6
23
ChaithanyaV. V.SugiyaN.AneeshK. S. (2015). Wild edible plants traditionally used by Kadar tribes of Vazhachal forest division, Thrissur, Kerala. J. Glob. Biosci. 4, 3344–3349.
24
ChandR.SinghA. N.NirmalaC. (2017). Ethnoecological survey of underutilized plant diversity of Hamirpur district, Himachal Pradesh, India: an edibility assessment. Environ. Ecol. Res.5, 13–29. 10.13189/eer.2017.050101
25
ChauhanD.ShrivastavaA. K.PatraS. (2014). Diversity of leafy vegetables used by tribal peoples of Chhattisgarh, India. Int. J. Curr. Microbiol. Appl. Sci.3, 611–622.
26
ChauhanS. H.YadavS.TakahashiT.LuczajL.D'CruzL.OkadaK. (2018). Consumption patterns of wild edibles by the vasavas: a case study from Gujarat, India. J. Ethnobiol. Ethnomed.14:57. 10.1186/s13002-018-0254-3
27
ChevalierA.MarinovaE, Peña-Chocarro L. (eds). (2014a). Plants and People: Choices and Diversity Through Time (Vol. 1). Oxford, UK: Oxbow Books.
28
ChevalierA.MarinovaE.Peña-ChocarroL. (2014b). Factors and issues in plant choice, in Plants and People: Choices and Diversity Through Time. Vol. 1. eds ChevalierA.MarinovaE.Peña-ChocarroL. (Oxford; Philadelphia: Oxbow Books), 3–12. 10.2307/j.ctvh1dwfp
29
ChorolS.AngchokD.AngmoP.TamchosT.SinghR. K. (2018). Traditional knowledge and heirloom root vegetables: food security in trans-Himalayan Ladakh, India. Indian J. Tradit. Knowl.17, 191–197
30
ChoudharyK.SinghM.PillaiU. (2008). Ethnobotanical survey of Rajasthan-an update. Am. Eurasian J. Bot.1, 38–45.
31
ChristiensenH. (2002). Ethnobotany of the Iban and the Kelabit. Videbaek: Joint Publication of Forest Department Sarawak, NEPCon and University of Aarhus
32
CookJ. A.VanderJagtD. J.PastuszynA.MounkailaG.GlewR. S.MillsonM.et al. (2000). Nutrient and chemical composition of 13 wild plant foods of Niger. J. Food Composit. Anal.13, 83–92. 10.1006/jfca.1999.0843
33
Cruz-GarcíaG. S. (2006). The mother–child nexus. Knowledge and valuation of wild food plants in Wayanad, Western Ghats, India. J. Ethnobiol. Ethnomed.2:39. 10.1186/1746-4269-2-39
34
Cruz-GarciaG. S.ErtugF. (2014). Introduction: wild food plants in the present and past, in Plants and People. Choices and Diversity Through Time, eds ChevalierA.MarinovaE.Peña-ChocarroL. (Oxford: Oxbow Books), 211–215.
35
Cruz-GarciaG. S.PriceL. L. (2011). Ethnobotanical investigation of ‘wild' food plants used by rice farmers in Kalasin, Northeast Thailand. J. Ethnobiol. Ethnomed.7:33. 10.1186/1746-4269-7-33
36
Cruz-GarciaG. S.PriceL. L. (2012). Weeds as important vegetables for farmers. Acta Soc. Bot. Pol.81, 397–403. 10.5586/asbp.2012.047
37
DeviM. H.SinghP. K.ChoudhuryM. D. (2014). Income generating plants of Keibul Lamjao National Park, Loktak Lake, Manipur and man-animal conflicts. Pleione8, 30–36.
38
DeviM. R.SalamS. (2016). Wild edible plants used by the Monsang Naga tribe of Manipur, India. Pleione10, 90–96.
39
DeviO. S.KomorP.DasD. (2010). A checklist of traditional edible bio-resources from Ima markets of Imphal Valley, Manipur, India. J. Threat. Taxa2, 1291–1296. 10.11609/JoTT.o2256.1291-6
40
DeweyK. G. (1981). Nutritional consequences of the transformation from subsistence to commercial agriculture in Tabasco, Mexico. Hum. Ecol.9, 151–187. 10.1007/BF00889132
41
DoganY.UguluI.DurkanN. (2013). Wild edible plants sold in the local markets of Izmir, Turkey. Pak. J. Bot.45, 177–184.
42
ErtugF. (2014). Wild plant food: routine dietary supplement or famine food? in Plants and People. Choices and Diversity Through Time, eds ChevalierA.MarinovaE.Peña-ChocarroL. (Oxford: Oxbow Books), 211–215.
43
EzellK. C.PearsallD. M.ZeidlerJ. A. (2006). Root and tuber phytoliths and starch grains document manioc (Manihot esculenta) arrowroot (Maranta arundinacea) and llerén (Calathea sp.) at the real alto site ecuador. Econ. Bot.60, 103–120. 10.1663/0013-0001(2006)60[103:RATPAS]2.0.CO;2
44
FAO (2010). The Second Report on the State of the World's Plant Genetic Resources for Food and Agriculture. Rome: Food and Agriculture Organization of the United Nations.
45
FAO (2012). The State of Food Insecurity in the World: Economic Growth is Necessary But Not Sufficient to Accelerate Reduction of Hunger and Malnutrition. Italy: Food and Agriculture Organization of the United Nations.
46
FAO and FHI 360. (2016). Minimum Dietary Diversity for Women: A Guide for Measurement.Rome.
47
FAOWFP, and IFAD . (2012). The State of Food Insecurity in the World 2012 Economic Growth is Necessary but Not Sufficient to Accelerate Reduction of Hunger and Malnutrition. Rome: FAO.
48
FatmaN.PanT. K. (2012). Checklist of wild edible plants of Bihar, India. Our Nat.10, 233–241. 10.3126/on.v10i1.7785
49
FowlerC.MooneyP. (1990). The Threatened Gene: Food, Politics, and the Loss of Genetic Diversity. Cambridge: Lutterworth Press.
50
GangteH. E.ThoudamN. S.ZomiG. T. (2013). Wild edible plants used by the Zou tribe in Manipur, India. Int. J. Sci. Res. Pub.3, 1–8.
51
GhatapanadiS. R.JohnsonN.RajasabA. H. (2011). Documentation of folk knowledge on medicinal plants of Gulbarga district, Karnataka. Indian. J. Tradit. Know.10, 349–353.
52
Ghosh-JerathS.SinghA.KambojP.GoldbergG.MagsumbolM. S. (2015). Traditional knowledge and nutritive value of indigenous foods in the oraon tribal community of Jharkhand: an exploratory cross-sectional study. Ecol. Food Nutr. 54, 493–519. 10.1080/03670244.2015.1017758
53
Ghosh-JerathS.SinghA.MagsumbolM. S.KambojP.GoldbergG. (2016). Exploring the potential of indigenous foods to address hidden hunger: nutritive value of indigenous foods of Santhal tribal community of Jharkhand, India. J. Hunger Environ. Nutr.11, 548–568. 10.1080/19320248.2016.1157545
54
GonzálezJ. A.García-BarriusoM.AmichF. (2011). The consumption of wild and semi-domesticated edible plants in the Arribes del Duero (Salamanca-Zamora, Spain): an analysis of traditional knowledge. Genet. Resour. Crop Evol.58, 991–1006. 10.1007/s10722-010-9635-8
55
GosdenC.HatherJ. G. (eds.). (2004). The Prehistory of Food: Appetites for Change. London: Routledge. 10.4324/9780203203385
56
GuralnikJ.EisenstaedtR. S.FerrucciL.KleinH.WoodmanR. (2004). Prevalence of anemia in persons 65 years and older in the United States: evidence for a high rate of unexplained anemia. Blood104, 2263–226810.1182/blood-2004-05-1812
57
HadjichambisA. C.Paraskeva-HadjichambiD.DellaA.Elena GiustiM.De PasqualeC.LenzariniC.et al. (2008). Wild and semi-domesticated food plant consumption in seven circum-Mediterranean areas. Int. J. Food Sci. Nutr.59, 383–414. 10.1080/09637480701566495
58
Hama-BaF.SibiriaN.PowellB.IckowitzA.MaunduP. (2017). Micronutrient content of wild vegetable species harvested in forested and non-forested areas in Southwest Burkina Faso. For. Res.6:213. 10.4172/2168-9776.100213
59
HarrisD. R.HillmanG. C. (2014). Foraging and Farming: the Evolution of Plant Exploitation. New York, NY: Routledge. 10.4324/9781315746425
60
HoroS.TopnoS. (2015). Lesser known wild leafy vegetables consumed by “Ho” tribes of W. Singhbhum district, Jharkhand, India. J. Med. Plants3, 155–159.
61
HuS. Y. (2005). Food Plants of China. Hongkong: The Chinese University Press.
62
HunterD.FanzoJ. (2013). Introduction: agricultural biodiversity, diverse diets and improving nutrition, in Diversifying Food and Diets, eds FanzoJ.HunterD.BorelliT.MatteiF. (New York, NY: Routledge), 33–46.
63
IckowitzA.PowellB.RowlandD.JonesA.SunderlandT. C. H. (2019). Agricultural intensification, dietary diversity, and markets in the global food security narrative. Glob. Food Secur.20, 9–16. 10.1016/j.gfs.2018.11.002
64
IckowitzA.RowlandD.PowellB.SalimM. A.SunderlandT. (2016). Forests, trees, and micronutrient-rich food consumption in Indonesia. PLoS ONE11:e0154139. 10.1371/journal.pone.0154139
65
IgnacimuthuS.AyyanarM. (2006). Ethnobotanical investigations among tribes in Madurai district of Tamil Nadu (India). J. Ethnobiol. Ethnomed.2:25. 10.1186/1746-4269-2-25
66
JainA.SinghH. B.BhattacharyyaP. R. (2012). The ethnobotany and nutritional values of wild rice [Zizania latifolia (Griseb.) Turcz. ex Stapf] (Poaceae) in Manipur. Indian J. Tradit. Know.11, 66–69
67
JainA.SundriyalM.RoshnibalaS.KotokyR.KanjilalP. B.SinghH. B.et al. (2011). Dietary use and conservation concern of edible wetland plants at indo-burma hotspot: a case study from northeast India. J. Ethnobiol. Ethnomed.7:29. 10.1186/1746-4269-7-29
68
JainA. K.TiwariP. (2012). Nutritional value of some traditional edible plants used by tribal communities during emergency with reference to Central India. Indian J. Tradit. Know.11, 51–57
69
JainS. K. (1964). Wild plant foods of the tribals of Bastar. Khadi Gramodyog10, 557–561.
70
JeevaS. (2009). Horticultural potential of wild edible fruits used by the Khasi tribes of Meghalaya. J. Hortic. For. 1, 182–192.
71
JeyaprakashK.AyyanarM.GeethaK. N.SekarT. (2011). Traditional uses of medicinal plants among the tribal people in Theni district (Western Ghats), Southern India. Asian Pac. J. Trop. Biomed.1, S20–S25. 10.1016/S2221-1691(11)60115-9
72
JonesA. D. (2017). Critical review of the emerging research evidence on agricultural biodiversity, diet diversity, and nutritional status in low- and middle-income countries. Nutr. Rev.75, 769–78210.1093/nutrit/nux040
73
KarA. (2004). Common wild vegetables of Aka tribe of Arunachal Pradesh. Indian J. Trad. Know.3, 305–313
74
KarA.BorthakurS. K. (2007). Wild vegetables sold in local markets of Karbi Anglong, Assam. Indian J. Tradit. Know.6, 169–172
75
KarA.BorthakurS. K. (2008). Wild vegetables of Karbi-anglong district, Assam. Nat. Prod. Rad.7, 448–460
76
KatewaS. S.ChaudharyB. L.JainA.GalavP. (2003). Traditional uses of plant biodiversity from Aravalli hills of Rajasthan. Indian J. Tradit. Knowl.2, 27–39
77
KatzE.LopezC. L.FleuryM.MillerR. P.PayêVDiasT.et al. (2012). No greens in the forest? Note on the limited consumption of greens in the Amazon. Acta Soc. Bot. Pol.81, 283–29310.5586/asbp.2012.048
78
KhanT. M.KakdeU. B. (2014). Biodiversity in wild vegetables of Konkan region - Maharashtra. Int. J. Res. Biosci. Agric. Technol.2, 226–240.
79
KhaundP.JoshiS. R. (2013). Wild edible macrofungal species consumed by the Khasi tribe of Meghalaya, India. Indian J. Nat. Prod. Res.4, 197–204.
80
KonsamS.ThongamB.HandiqueA. K. (2016). Assessment of wild leafy vegetables traditionally consumed by the ethnic communities of Manipur, northeast India. J. Ethnobiol. Ethnomed.12:9. 10.1186/s13002-016-0083-1
81
KumarA. (2013). Ethnobotanical study of wild vegetables used by rural communities of Kannauj district, Uttar Pradesh, India. Emir. J. Food Agric.24, 760–766. 10.9755/ejfa.v25i10.16403
82
KumarP. G. M.ShiddamallayyaN. (2014). Documentation of wild plant tubers as food resources in Hassan district, Karnataka. Int. J. Appl. Biol. Pharm. Technol.5, 90–95
83
KumarV.JainS. K. (2002). Plant products in some tribal markets of central India. Econ. Bot.56, 242–245. 10.1663/0013-0001(2002)056[0242:PPISTM]2.0.CO;2
84
LabadariosD. (2005). Malnutrition in the developing world: the triple burden. South Afr. J. Clin. Nutr.18, 119–121. 10.1080/16070658.2005.11734052
85
LeontiM.NebelS.RiveraD.HeinrichM. (2006). Wild gathered food plants in the European Mediterranean: a comparative analysis. Econ. Bot.60, 130–142. 10.1663/0013-0001(2006)60[130:WGFPIT]2.0.CO;2
86
LeontiM.RamirezR.SticherF.HeinrichO. M. (2003). Medicinal flora of the Popoluca, México: a botanico-systematical perspective. Econ. Bot.57, 218–230. 10.1663/0013-0001(2003)057[0218:MFOTPM]2.0.CO;2
87
LohJ.HarmonD. (2005). A global index of biocultural diversity. Ecol. Indicat.5, 231–24110.1016/j.ecolind.2005.02.005
88
LuczajL. (2008). Archival data on wild food plants eaten in Poland in 1948. J. Ethnobiol. Ethnomed.4:4. 10.1186/1746-4269-4-4
89
LuczajL. (2012). Ethnobotanical review of wild edible plants of Slovakia. Acta Soc. Bot. Pol.81, 245–255. 10.5586/asbp.2012.030
90
LykkeA. M.MertzO.GanabaS. (2002). Food consumption in rural Burkina Faso. Ecol. Food Nutr.41, 119–153. 10.1080/03670240214492
91
MaffiL.WoodleyE. (2012). Biocultural Diversity Conservation: A Global Sourcebook. London; Washington, DC: Routledge. 10.4324/9781849774697
92
MahadkarS.ValviS.RathodV. (2012). Nutritional assessment of some selected wild edible plants as a good source of mineral. Asian J. Plant Sci. Res.2, 468–472.
93
MahapatraA. K.PandaP. C. (2012). Wild edible fruit diversity and its significance in the livelihood of indigenous tribals: evidence from eastern India. Food Secur.4, 219–234. 10.1007/s12571-012-0186-z
94
MaikhuriR. K.SemwalD. L.SinghA.NautiyalD. C. (1994). Wild fruits as a contribution to sustainable rural development: a case study from the Garhwal Himalaya. Int. J. Sustain. Dev. World Ecol.1, 56–68. 10.1080/13504509409469861
95
ManiM. S. (1974). Biogeographical evolution in India, in Ecology and Biogeography in India, ed ManiM. S. (Dordrecht: Springer), 698–724. 10.1007/978-94-010-2331-3_24
96
MaoA. A.HynniewtaT. M.SanjappaM. (2009). Plant wealth of Northeast India with reference to ethnobotany. Indian J. Tradit. Know.8, 96–103.
97
MazharF.BucklesD.SatheeshP. V.AkhterF. (2007). Food Sovereignty and Uncultivated Biodiversity in South Asia. New Delhi, India: Academic Foundation.
98
MedhiP.BorthakurS. K. (2012). Phytoresources from North Cachar hills of Assam, India-VII: semi-domesticated and protected plants. Pleione6, 66–79.
99
MedhiP.SarmaA.BorthakurS. K. (2014). Wild edible plants from the Dima Hasao district of Assam, India. Pleione8, 133–148.
100
MelamedY.KislevM. E.GeffenE.Lev-YadunS.Goren-InbarN. (2016). The plant component of an acheulian diet at Gesher Benot Ya‘aqov, Israel. Proc. Natl. Acad. Sci. U.S.A.113, 14674–14679. 10.1073/pnas.1607872113
101
MishraM.ShrivastavaM. (2015). Trade of minor forest products in the rural markets of central India. Biol. Forum7, 516–521.
102
MishraM. L.SoodS.ShuklaU. N. (2018). Phyto-nutritional and mineral composition of Indian horse chestnut (Aesculus indica) seeds. J. Pharm. Phytochem.7, 2159–2162. 10.20546/ijcmas.2018.709.270
103
MishraN.PandaT.PradhanB. K.RoutS. D.MohantyR. B.KishorA.et al. (2016). Indigenous knowledge in utilization of wetland plants of Bhadrak district, Odisha, India. Indian J. Nat. Prod. Resour.7, 82–89.
104
MishraS.SharmaS.VasudevanP. (2015). Role of edible food plants in women's nutrition and health, in Women, Technology and Development, eds VasudevanP.SharmaS.SharmaV. P.VermaM. (Narosa Publishing House), 1–17.
105
MisraR. C.SahooH. K.PaniD. R.BhandariD. C. (2013). Genetic resources of wild tuberous food plants traditionally used in Similipal biosphere reserve, Odisha, India. Genet. Resour. Crop Evol.60, 2033–2054. 10.1007/s10722-013-9971-6
106
MisraS.MaikhuriR. K.KalaC. P.RaoK. S.SaxenaK. G. (2008). Wild leafy vegetables: a study of their subsistence dietetic support to the inhabitants of Nanda Devi biosphere reserve, India. J. Ethnobiol. Ethnomed.4:15. 10.1186/1746-4269-4-15
107
MoermanD. E. (1996). An analysis of the food plants and drug plants of native North America. J. Ethnopharmacol.52, 1–22. 10.1016/0378-8741(96)01393-1
108
MohammedS.KaseraP. K.ShuklaJ. K. (2004). Unexploited plants of potential medicinal value from the Indian Thar desert. Nat. Prod. Rad.3, 69–74.
109
MohanV. R.KalidassC. (2010). Nutritional and antinutritional evaluation of some unconventional wild edible plants. Trop. Subtrop. Agroecosyst.12, 495–506.
110
MukherjeeS.ChaturvediS. S. (2016). Uitilization of wild edible trees in fringe area of Neora-valley national park, Darjeeling, in International Conference on Agriculture, Food Science, Natural Resource Management and Environmental Dynamics: The Technology, People and Sustainable Development. (Mohanpur, Nadia, West Bengal, India).
111
MuruganM.RajX. J.KumarG. P.SunilG.SinghS. B. (2010). Phytofoods of Nubra valley, Ladakh-the cold desert. Indian J. Tradit. Know.9, 303–308.
112
NairR.AgrawalV. (2017). Nutritive values and uses of some important arid zone fruit trees of Madhya Pradesh. Int. J. Chem. Stud.5, 399–404.
113
NamsaN. D.MandalM.TangjangS.MandalS. C. (2011). Ethnobotany of the Monpa ethnic group at Arunachal Pradesh, India. J. Ethnobiol. Ethnomed.7:31. 10.1186/1746-4269-7-31
114
NarayananM. R.AnilkumarN.BalakrishnanV.SivadasanM.AlfarhanH. A.AlatarA. A. (2011). Wild edible plants used by the Kattunaikka, Paniya and Kuruma tribes of Wayanad district, Kerala, India. J. Med. Plants Res.5, 3520–3529.
115
NathA.MaitiG. G. (2011). An ethnobotancial report on less-known leafy vegetables consumed by different communities of Barak valley, Assam, India. Ecobios4, 45–55.
116
NayarM. P. (1996). Hotspots of Endemic Plants of India, Nepal and Bhutan. Trivandrum: Tropical Botanic Garden and Research Institute.
117
NazarudeenA. (2010). Nutritional composition of some lesser-known fruits used by the ethnic communities and local folks of Kerala. Indian J. Tradit. Know.9, 398–402
118
NeogiB.PrasadM. N.RaoR. R. (1989). Ethnobotany of some weeds of Khasi and Garo hills, Meghalaya, Northeastern India. Econ. Bot. 43, 471–479. 10.1007/BF02935921
119
NongdamP.TikendraL. (2014). The nutritional facts of bamboo shoots and their usage as important traditional foods of northeast India. Int. Sch. Res. Notices2014:679073. 10.1155/2014/679073
120
OgleB. M. (2001). Wild Vegetables and Micronutrient Nutrition: Studies on the Significance of Wild Vegetables in Women's Diets in Vietnam. (Doctoral dissertation, Acta Universitatis Upsaliensis).
121
OgleB. M.GrivettiL. E. (1985a). Legacy of the chameleon: edible wild plants in the kindom of Swaziland, Southern Africa. A cultural, ecological, nutritional study. part II - demographics, species availability and dietary use, analysis by ecological zone. Ecol. Food Nutr.17, 1–30. 10.1080/03670244.1985.9990879
122
OgleB. M.GrivettiL. E. (1985b). Legacy of the chameleon: edible wild plants in the kingdom of Swaziland, Southern Africa. A cultural, ecological, nutritional study. part IV-nutritional analysis and conclusions. Ecol. Food Nutr.17, 41–64. 10.1080/03670244.1985.9990881
123
OgleB. M.TuyetH. T.DuyetH. N.DungN. N. X. (2003). Food, feed or medicine: the multiple functions of edible wild plants in Vietnam. Econ. Bot.57, 103–117. 10.1663/0013-0001(2003)057[0103:FFOMTM]2.0.CO;2
124
PadaliaK. (2015). Gewai saag: a folk medicine used by the tribal people of Central Himalayan region. Indian J. Trad. Know.1, 144–146.
125
PadochC.SunderlandT. (2014). Managing landscapes for food security and enhanced livelihoods: building upon a wealth of local experience. Unasylva64:2013/2.
126
PandaT. (2014). Traditional knowledge on wild edible plants as livelihood food in Odisha, India. J. Biol. Earth Sci.4, B144–B159
127
PandeyA.SinghS.SinghR.MavinkurveR. G. (2015). Use of indigenous plants in traditional health care systems and economic use by Mishing tribe of Jorhat, Assam, India. World J. Pharm. Sci.4, 1277–1289.
128
PandeyA. K.BoraH. R. (1997). Edible plants of Shan tribe of Assam. Anc. Sci. Life16, 258–276
129
PandeyG. (1998). Wild temperate fruit plants of Himachal Pradesh, India. Plant Genet. Resour. Newslett.116, 9–11.
130
PandeyK. C.PandeN. (2016). Ethnobotanical documentation of wild edible plants used by Gujjar community of Tarai West forest division Ramnagar, Nainital, India. Curr. World Environ.11, 808–81810.12944/CWE.11.3.16
131
PandeyR. K.SainiS. K. (2007). Edible plants of tropical forests among tribal communities of Madhya Pradesh. Indian J. Tradit. Know.6, 185–190
132
PantS.SamantS. S. (2010). Ethnobotanical observations in the Mornaula reserve forest of Komoun, West Himalaya, India. Ethnobot. Leaflets14, 193–217
133
Pardo-de-SantayanaM.TardíoJ.BlancoE.CarvalhoA. M.LastraJ. J.San MiguelE.et al. (2007). Traditional knowledge of wild edible plants used in the northwest of the Iberian Peninsula (Spain and Portugal): a comparative study. J. Ethnobiol. Ethnomed.3:27. 10.1186/1746-4269-3-27
134
ParinithaM.HarishG. U.VivekN. C.MaheshT.ShivannaM. B. (2004). Ethno-botanical wealth of Bhadra wild life sanctuary in Karnataka. Indian J. Tradit. Know.3, 37–50
135
ParisaraN.KiranB. R. (2016). Enumeration of leafy vegetables of BhadravathiTaluk, Karnataka. Int. J. Sci. Res. Sci. Technol.2, 32–35.
136
PatiriB.BorahA. (2007). Wild Edible Plants of Assam. Guwahati: Geetakhi Printers and Publishers.
137
PaumgartenF.ShackletonC. M. (2011). The role of non-timber forest products in house- hold coping strategies in South Africa: the influence of household wealth and gender. Popul. Environ.33, 108–131. 10.1007/s11111-011-0137-1
138
PembertonR. W.LeeN. S. (1996). Wild food plants in South Korea; market presence, new crops, and exports to the United States. Econ. Bot.50, 57–70. 10.1007/BF02862113
139
PhozeN. L.KumarY.MyrbohB. (2001). Survey and assessment of floral diversity on wild edible plants from Senapati district of Manipur, Northeast India. J. Biodiv. Environ. Sci.1, 50–62.
140
PingaliP. (2015). Agricultural policy and nutrition outcomes – getting beyond the pre-occupation with staple grains. Food Secur.7, 583–591. 10.1007/s12571-015-0461-x
141
Pinstrup-AndersenP. (2007). Agricultural research and policy for better health and nutrition in developing countries: a food systems approach. Agric. Econ.37, 187–198. 10.1111/j.1574-0862.2007.00244.x
142
PowellB.ThilstedS.IckowitzA.TermoteC.SunderlandT.HerforthA. (2015). Improving diets with wild and cultivated biodiversity from across the landscape. Food Secur.7, 535–554. 10.1007/s12571-015-0466-5
143
PradhanB. K.BadolaH. K. (2008). Ethnomedicinal plant use by Lepcha tribe of Dzongu valley, bordering Khangchendzonga biosphere reserve, in north Sikkim, India. J. Ethnobiol. Ethnomed.4:22. 10.1186/1746-4269-4-22
144
PrettyJ. N. (1995). Regenerating Agriculture: Policies and Practice for Sustainability and self-reliance. Regenerating agriculture: policies and Practice for Sustainability and Self-reliance. London: Earthscan Publications; Washington, DC: National Academy Press; Bangalore: ActionAid and Vikas.
145
PriceL. L. (2006). Wild food plants in farming environments with special reference to Northeastern Thailand, food as functional and medicinal, and the social roles of women, in Eating and Healing: Traditional Food as Medicine, eds PieroniA.PriceL. L. (New York; London; Oxford: Food Products Press), 65–100.
146
PugalenthiM.VadivelV.GurumoorthiP.JanardhananK. (2004). Comparative nutritional evaluation of little known legumes, Tamarindus indica, Erythrina indica and Sesbania bispinosa. Trop. Subtrop. Agroecosyst.4, 107–123.
147
RadhaB.SinghR. D.TiwariJ. K.TiwariP.GairolaA. (2013). Wild edible plant resources of the Lohba range of Kedarnath forest division (KFD), Garhwal Himalaya, India. Int. Res. J. Biol. Sci.2, 65–73.
148
RajasabA. H.IsaqM. (2004). Documentation of folk knowledge on edible wild plants of North Karnataka. Indian J. Tradit. Know.3, 419–429.
149
RajyalakshmiP.VenkatalaxmiK.VenkatalakshmammaK.JyothsnaY.DeviK. B.SuneethaV. (2001). Total carotenoid and beta-carotene contents of forest green leafy vegetables consumed by tribals of south India. Plant Foods Hum. Nutr.56, 225–238. 10.1023/A:1011125232097
150
RamachandranV. S. (2007). Wild edible plants of the Anamalais, Coimbatore district, western Ghats, Tamil Nadu. Indian J. Tradit. Know.6, 173–176
151
RamachandranV. S.JosephS.ArunaR. (2009). Ethnobotanical studies from Amaravathy range of Indira Gandhi wildlife sanctuary, Western Ghats, Coimbatore District, Southern India. Ethnobot. Leaflets13, 1069–1087.
152
RanaJ. C.PradheepK.ChaurasiaO. P.SoodS.SharmaR. M.SinghA.et al. (2012). Genetic resources of wild edible plants and their uses among tribal communities of cold arid region of India. Genet. Resour. Crop Evol.59, 135–149. 10.1007/s10722-011-9765-7
153
RanfaA.MauriziA.RomanoB.BodesmoM. (2014). The importance of traditional uses and nutraceutical aspects of some edible wild plants in human nutrition: the case of Umbria (central Italy). Plant Biosyst.148, 297–306. 10.1080/11263504.2013.770805
154
RasingamL. (2012). Ethnobotanical studies on the wild edible plants of Irula tribes of Pillur valley, Coimbatore district, Tamil Nadu, India. Asian Pac. J. Trop. Biomed.2, S1493–S1497. 10.1016/S2221-1691(12)60443-2
155
RathoreM. (2009). Nutrient content of important fruit trees from arid zone of Rajasthan. J. Hortic. For.1, 103–108.
156
RowlandD.IckowitzA.PowellB.NasiR.SunderlandT. C. H. (2016). Forest foods and healthy diets: quantifying the contributions. Environ. Conserv.44, 102–114. 10.1017/S0376892916000151
157
Royal Society (2009). Reaping the Benefits: Science and the Sustainable Intensification of Global Agriculture. London: The Royal Society.
158
SamyduraiP.ThangapandianV.AravinthanV. (2012). Wild habits of Kolli hills being staple food of inhabitant tribes of Eastern Ghats, Tamil Nadu, India. Indian J. Nat. Prod. Resour.3, 432–437
159
SarvalingamA.RajendranA.SivalingamR. (2015). Wild edible plant resources used by the Irulas of the Maruthamalai Hills, Southern Western Ghats, Coimbatore, Tamil Nadu. Indian J. Nat. Prod. Resour.5, 198–201.
160
SasiR.RajendranA. (2012). Diversity of wild fruits in Nilgiri hills of the Southern Western Ghats: ethnobotanical aspects. Int. J. Appl. Biol. Pharm. Technol.3, 82–87.
161
SasiR.RajendranA.MaharajanM. (2011). Wild edible plant diversity of Kotagiri hills - a part of Nilgiri biosphere reserve, Southern India. J. Res. Biol.2, 80–87.
162
SathyavathiR.JanardhananK. (2014). Wild edible fruits used by Badagas of Nilgiri district, Western Ghats, Tamilnadu, India. J. Med. Plants Res.8, 128–132. 10.5897/JMPR11.445
163
SatterM. M. A.KhanM. M. R. L.JabinS. A.AbedinN.IslamM. F.ShahaB. (2016). Nutritional quality and safety aspects of wild vegetables consume in Bangladesh. Asian Pac. J. Trop. Biomed.6, 125–131. 10.1016/j.apjtb.2015.11.004
164
SatyavaniS.SatyavathiK.PadalS. D. (2015). Wild edible plants used for indigenous community of North–Coastal Andhra Pradesh, India. BMR Phytomed.2, 1–7
165
ScoonesI.MelnykM.PrettyJ. N. (1992). The Hidden Harvest: Wild Foods in Agricultural Systems. A Bibliography and Literature Review.London: International Institute for Environment and Development.
166
SheelaK.NathK. G.VijayalakshmiD.YankanchiG. M.PatilR. B. (2004). Proximate composition of underutilized green leafy vegetables in Southern Karnataka. J. Hum. Ecol.15, 227–229. 10.1080/09709274.2004.11905698
167
ShinT.FujikawaK.MoeA. Z.UchiyamaH. (2018). Traditional knowledge of wild edible plants with special emphasis on medicinal uses in Southern Shan State, Myanmar. J. Ethnobiol. Ethnomed.14:48. 10.1186/s13002-018-0248-1
168
SimopoulosA. P. (2004). Omega-3 fatty acids and antioxidants in edible wild plants. Biol. Res.37, 263–277. 10.4067/S0716-97602004000200013
169
SinghA.SatankerN.KushwahaM.DisoriyaR.GuptaA. K. (2013). Ethno-botany and uses of non-graminaceous forage species of Chitrakoot region of Madhya Pradesh. Indian J. Nat. Prod. Resour.4, 425–431.
170
SinghB. K.PathakK. A.RamakrishnaY. (2013). Underutilized Vegetable Crops and Spices of Mizoram: Needs Exploration and Utilization. Developing the Potential of Underutilized Horticultural Crops of Hill Regions. New Delhi: Today & Tomorrow's Printers and Publishers. 217–232.
171
SinghH. B.AroraR. K. (1978). Wild edible plants of India. New Delhi: ICAR.
172
SinghJ.RajasekaranA.NegiA. K.PalaN. A. (2014). Wild vegetable plants used by tribal people of Kinnaur district, Himachal Pradesh, India. Int. J. Usufructs Manage.15, 47–56.
173
SinghV. N.ChanuL. I.BaruahM. K. (2011). An ethnobotanical study of Chirus-A less known tribe of Assam. Indian J. Tradit. Know.10, 572–574.
174
SinhaR.LakraV. (2005). Wild tribal food plants of Orissa. Indian J. Tradit. Know.4, 246–252
175
SinhaR.LakraV. (2007). Edible weeds of tribals of Jharkhand, Orissa and West Bengal. Indian J. Tradit. Know. 6, 217–222
176
SrivastavaT. N. (1998). Wild edible plants of Jammu & Kashmir state–an ethno-botanical study. Anc. Sci. Life. 7:201.
177
SujarwoW.ArinasaI. B. K.CanevaG.GuarreraP. M. (2014). Traditional knowledge of wild and semi-wild edible plants used in Bali (Indonesia) to maintain biological and cultural diversity, Plant Biosyst.150, 971–97610.1080/11263504.2014.994577
178
SundriyalM.SundriyalD. C. (2001). Wild edible plants of the Sikkim himalaya: nutritive values of selected species. Econ. Bot.55, 377–39010.1007/BF02866561
179
SundriyalM.SundriyalR. C. (2003). Underutilized edible plants of the Sikkim himalaya: need for domestication. Curr. Sci.25, 731–736.
180
SuthariS.SreeramuluN.OmkarK.RajuV. S. (2014). The climbing plants of northern Telangana in India and their ethnomedicinal and economic uses. Indian J. Plant Sci.3, 86–100.
181
SwarnkarS.KatewaS. S. (2008). Ethnobotanical observation on tuberous plants from tribal area of Rajasthan (India). Ethnobot. Leaflets12, 647–666. 10.17348/era.12.0.211-235
182
TardíoJ.Pardo-de-SantayanaM.MoralesR. (2006). Ethnobotanical review of wild edible plants in Spain. Bot. J. Lin. Soc.152, 27–71. 10.1111/j.1095-8339.2006.00549.x
183
The Plant List (2010). Version 1. Published on the Internet. Available online at: http://www.theplantlist.org/ (accessed January 1)
184
ThomasM.SahuP.ShrivastavaA.HussainZ. (2011). Biodiversity and livelihood options of people in Chambal ravine of Morena district, Madhya Pradesh, India. J. Trop. For.27, 40–56.
185
TiwariJ. K.BallabhaR.TiwariP. (2010). Some promising wild edible plants of Srinagar and its adjacent area in Alaknanda valley of Garhwal Himalaya, India. J. Am. Sci.6, 167–174.
186
TurnerN. J.LuczajL.MiglioriniP.PieroniA.DreonA. L.EnricaL.et al. (2011). Edible and tended wild plants, traditional ecological knowledge and agroecology. Crit. Rev. Plant Sci.30, 198–225. 10.1080/07352689.2011.554492
187
UpretiK.TewariL. M.PangteyY. P.JalalJ. S. (2010). Diversity and distribution of wild edible fruit plants of Uttarakhand, in Nainital Biodiversity Potentials of the Himalaya eds TewariL. M.PangteyY. P. S.TewariG. (Gyanodaya Prakashan, Nainital), 157–196.
188
UusikuN. P.OelofseA.DuoduK. G.BesterM. J.FaberM. (2010). Nutritional value of leafy vegetables of sub-Saharan Africa and their potential contribution to human health: a review. J. Food Composit. Anal.23, 499–509. 10.1016/j.jfca.2010.05.002
189
VikneshwaranD.VijiM.LakshmiK. R. (2008). A survey of the ethnomedicinal flora of the Sirumalai hills, Dindugul district, India. Ethnobot. Leaflets12, 948–953.
190
VishwakarmaK. L.DubeyV. (2011). Nutritional analysis of wild edible herbs used in eastern Chhattisgarh, India. Emir. J. Food Agric.15, 554–560.
191
Von GrebmerK. A.SaltzmanE.BirolD.WiesmannN.PrasaiS.YinY.et al. (2014). 2014 Global Hunger Index: the Challenge of Hidden Hunger. Washington, DC; Dublin: Welthungerhilfe, International Food Policy Research Institute, and Concern Worldwide, Bonn.
192
WillsR. B.LimJ. S.GreenfieldH.Bayliss-SmithT. (1983). Nutrient composition of taro (Colocasia esculenta) cultivars from the Papua New Guinea highlands. J. Sci. Food Agric.34, 1137–1142. 10.1002/jsfa.2740341015
193
World Food Summit (1996). Rome Declaration on World Food Security. Rome.
194
World Health Organization (2008). Indicators for Assessing Infant and Young Child Feeding Practices: Part 1 Definitions. Switzerland: Geneva.
195
WunderS.BörnerJ.ShivelyG.WymanM. (2014). Safety nets, gap filling and forests: a global-comparative perspective. World Dev.64(Suppl. 1): S29–S42. 10.1016/j.worlddev.2014.03.005
196
YakangB.GajurelP. R.PotsangbamS.BhuyanL. R. (2013). Account of common and traditional non-timber forest products used by Apatani tribe of Arunachal Pradesh, India. Pleione7, 514–529.
197
YuhlungC. C.BhattacharyyaM. (2014). Practice of ethno-medicine among the Chothe tribe of Manipur, North-East India. Int. J. Pharm. Biol. Arch.5, 138–149.
198
YumnamJ. Y.BhuyanS. I.KhanM. L.TripathiO. P. (2011). Agro-diversity of East Siang-Arunachal Pradesh, Eastern Himalaya. Asian J. Agric. Sci.3, 317–326.
199
ZhangY.LuX.ZengS.HuangX.GuoZ.ZhengY.et al. (2015). Nutritional composition, physiological functions and processing of lotus (Nelumbo nucifera Gaertn.) seeds: a review. Phytochem. Rev.14, 321–334. 10.1007/s11101-015-9401-9
Summary
Keywords
wild uncultivated plants, edible flora, sustainability, food system, hidden hunger, micronutrient, leafy greens, nutritional security
Citation
Ray A, Ray R and Sreevidya EA (2020) How Many Wild Edible Plants Do We Eat—Their Diversity, Use, and Implications for Sustainable Food System: An Exploratory Analysis in India. Front. Sustain. Food Syst. 4:56. doi: 10.3389/fsufs.2020.00056
Received
23 September 2019
Accepted
09 April 2020
Published
11 June 2020
Volume
4 - 2020
Edited by
Kathleen L. Hefferon, Cornell University, United States
Reviewed by
Chunlin Long, Minzu University of China, China; Indra Dutt Bhatt, Govind Ballabh Pant National Institute of Himalayan Environment and Sustainable Development, India; Lukasz Luczaj, University of Rzeszow, Poland
Updates
Copyright
© 2020 Ray, Ray and Sreevidya.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Avik Ray avikray@ceibatrust.org
This article was submitted to Nutrition and Sustainable Diets, a section of the journal Frontiers in Sustainable Food Systems
†ORCID: Avik Ray orcid.org/0000-0003-1662-7679
Disclaimer
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.