ORIGINAL RESEARCH article

Front. Sustain. Food Syst., 11 June 2020

Sec. Nutrition and Sustainable Diets

Volume 4 - 2020 | https://doi.org/10.3389/fsufs.2020.00056

How Many Wild Edible Plants Do We Eat—Their Diversity, Use, and Implications for Sustainable Food System: An Exploratory Analysis in India

  • Center for studies in Ethnobiology, Biodiversity, and sustainability (CEiBa), Malda, India

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

ReferencesBroad 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 partsFamilySpecies
Total1841,403
Seeds39155
Leaves or shoots134740
Flowers59153
Fruits110657
Underground parts70219
Others69167

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

SpeciesNumber of studies mentioning useRFC
Oxalis corniculata410.39
Amaranthus spinosus350.33
Phyllanthus emblica330.31
Colocasia esculenta310.295
Solanum americanum310.295
Centella asiatica310.295
Amaranthus viridis290.28
Chenopodium album280.27
Dioscorea bulbifera270.26
Commelina benghalensis260.25
Alternanthera sessilis260.25
Dioscorea pentaphylla260.25
Ziziphus jujuba240.23
Portulaca oleracea230.22
Senna tora220.22
Boerhavia diffusa220.22
Ipomoea aquatica220.22
Ficus racemosa210.2
Tamarindus indica210.2
Asparagus racemosus210.2
Aegle marmelos210.2
Diplazium esculentum210.2
Solanum torvum200.19
Moringa oleifera190.181
Spondias pinnata190.181

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

SpeciesNumber of edible partsRUV
Nymphaea nouchali Burm.f.61
Nymphaea rubra Roxb. ex Andrews50.83
Cannabis sativa L.50.83
Nelumbo nucifera Gaertn.40.67
Tamarindus indica L.40.67
Justicia adhatoda L.40.67
Spondias pinnata (L. f.) Kurz40.67
Ensete superbum (Roxb.) Cheesman40.67
Typha domingensis Pers.40.67
Bauhinia variegata L.40.67
Aesculus indica (Wall. ex Cambess.) Hook.40.67
Phyllanthus emblica L.40.67

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

SpeciesTotal number of citations of all partsCPP(se)CPP(l-sh)CPP(fl)CPP(fr)CPP(u)
Oxalis corniculata410.0240.8040.0240.1210
Amaranthus spinosus3500.971000
Phyllanthus emblica330.030.0610.87900
Colocasia esculenta5300.3770.11300.433
Solanum americanum3900.48700.5130
Centella asiatica3400.853000
Amaranthus viridis300.0670.933000
Chenopodium album300.0670.933000
Dioscorea bulbifera2900.03400.0340.896
Commelina benghalensis2700.852000.111
Alternanthera sessilis2601000
Dioscorea pentaphylla27000.07400.889
Ziziphus jujuba260.0380.11500.8460
Portulaca oleracea2200.909000
Senna tora230.0860.8260.0430.0430
Boerhavia diffusa2400.79200.0420.083
Ipomoea aquatica2300.95700.0430
Ficus racemosa230000.9130.043
Tamarindus indica330.1520.2420.0910.5150
Asparagus racemosus2200.0910.0910.0450.773
Aegle marmelos2200.09100.0910
Diplazium esculentum2001000
Solanum torvum2000.0500.950
Moringa oleifera300.0330.40.2330.3330
Spondias pinnata220.0450.0910.0910.7270

CPP value for selected plants with highest RFC value.

Table 4B

SpeciesTotal number of citation of all partsCPP(se)CPP(l-sh)CPP(fl)CPP(fr)CPP(u)
Colocasia esculenta5300.3770.11300.434
Phyllanthus emblica330.0300.06100.8790
Tamarindus indica330.1520.2420.0910.5150
Nelumbo nucifera320.2180.1560.18700.406
Moringa oleifera300.0330.40.2330.3330
Nymphaea nouchali250.120.160.20.120.24
Spondias pinnata210.0480.0950.0950.7620
Bauhinia variegata1600.250.62500.0625
Euryale ferox140.3570.35700.1420.071
Ensete superbum130.0770.3080.2310.3070
Ficus hispida1300.1530.07710
Dendrocalamus strictus120.1670.5830.08300.167
Typha domingensis110.0910.2720.36200.273
Rotheca serrata1100.4550.2730.0910.182
Solena amplexicaulis1100.18200.5450.273
Justicia adhatoda1000.50.30.10.1
Cannabis sativa90.3330.3330.1110.1110
Cajanus scarabaeoides90.4440.22200.2220.111
Alpinia galanga90.1100.2200.67
Nymphaea rubra80.250.12500.250.25
Borassus flabellifer80.1250.1250.1250.6250
Moringa concanensis700.4280.2850.2850
Holostemma ada-kodien600.3330.1670.1670.333
Dregea volubilis600.3330.1670.50
Fagopyrum acutatum60.1670.667000.167
Allium humile500.60.200.2
Taraxacum campylodes500.40.200.2
Flemingia procumbens500.200.20.6
Aesculus indica50.2000.40.2
Leea asiatica5000.40.40.2
Abutilon indicum50.20.40.200.2
Malva verticillata50.20.6000.2
Murraya paniculata400.250.250.50
Boehmeria glomerulifera300.3330.3330.3330
Urtica parviflora300.3330.33300.333
Allium carolinianum300.3330.33300.333
Allium jacquemontii300.3330.33300.333
Allium tuberosum300.3330.33300.333
Trichosanthes tricuspidata30.3330.333000.333
Fagopyrum acutatum30.3330.333000.333

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 speciesHigh priority speciesMedium to high priority species
Colocasia esculenta (L.) SchottAegle marmelos (L.) CorrêaAesculus indica (Wall. ex Cambess.) Hook.
Phyllanthus emblica L.Alternanthera sessilis (L.) R.Br. ex DC.Bauhinia variegata L.
Spondias pinnata (L. f.) KurzAmaranthus 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 speciesPartsVit AVit B1Vit B2Vit CVit ECaFeZnNaKCuPMgMnSeFolic acid
Aegle marmelosFr1860.011.2XX850.6XX0.6X31.8XXXX
Aerva lanataL, Sh21.76XX19X32222.060.6510.4XXXXXX0.04
Aesculus indicaSeXXXXX8.208.50705.9X81.000.6XX0.5XX
Agaricus sp. (Chiple)Fruit bodyXXXXX1.8420.130.730.0531.920.070.470.23XXX
Agaricus sp. (Patpate)Fruit bodyXXXXX1.530.110.60.062.170.090.760.34XXX
Alternanthera sessilisL, Sh1.9200.1417X5101.63XXXXXXXXX
Amaranthus spinosusL, Sh3.560X33X80022.9XXXXXXXXX
Amaranthus tricolorL, Sh5.520.030.399X3973.490.18230XXXXXX0.14
Amaranthus viridisL, ShXXX179X33018.7XXXXXXXXX
Antidesma acidumL, ShXXXXX1717XXXXXXXXXX
Aralia leschenaultiiFrXXXXX0.310.6X0.61.89X0.470.25XXX
Ardisia macrocarpaFrXXXXX0.290.020.310.040.890.070.130.31XXX
Arisaema utileFrXXXXX0.920.83X0.092.4X0.690.62XXX
Artocarpus lakoochaFr0.250.020.15135X500.05XXXXXXXXX
Baccaurea ramifloraFrXXX0.27X0.160.080.60.040.730.080.130.5XXX
Bambusa bambosL, Sh00.080.195X200.1XXXXXXXXX
Bambusa tuldaL, ShXXX1.420.614.063.190.7219.964080.44XXXXX
Bauhinia purpureaL, ShXXXXX312XXXXXXXXXX
Boerhaavia diffusaL, Sh16.01XX12X20210.680.4139.4XXXXXX0.02
Cannabis sativaL, ShX0.40.1X90145147128592X4837XX
Carissa carandasFrXXXXX21XXXXXXXXXX
Castanopsis indicaFrXXXXX15402.61.530.034.330.778012.682.350.0006X
Celosia argenteaL, ShXXXXX323XXXXXXXXXX
Centella asiaticaL, Sh0.50.53X5X23155.661.925.2XXXXXX0.01
Chenopodium albumL, Sh1.740.010.1435X1504.2XXXXXXXXX
Choerospondias axillarisFrXXX0.04X1.580.110.830.040.670.060.160.68XXX
Colocasia antiquorumL, Sh5.920.220.2612X22710XXXXXXXXX
Colocasis esculentaUXXXXX191.11.71340XX28XXX
Commelina benghalensisL, ShXXXXX1431.6 ±ramya 6.41115.92 ±ramya 5.512.68 ±ramya 0.17200 ±ramya 7.02390 ±ramya 15.522.72 ±ramya 0.09X220.8 ±ramya 4.157.98 ±ramya 0.26XX
Crotalaria junceaL, ShXXXXX200XXXXXXXXXX
Dendrocalamus strictusL, ShXXX2.430.58139.52.91X0.08XX58.130.17XXX
Dioscorea bulbiferaU0.3XX4X204.090.380.08XXXXXX0.028
Diospyros melanoxylonFr0.3610.010.041X600.5XXXXXXXXX
Diplazium esculentumFrXXXXX1.020.560.580.082.370.040.50.51XXX
Diploknema butyraceaFrXXX0.03X0.820.180.860.070.820.040.090.61XXX
Elaeagnus latifoliaFrXXX0.07X1.470.181.190.050.910.050.090.54XXX
Elaeagnus rhamnoidesFrXXX0.26X0.170.060.88XX0.020.310.31XXX
Elaeocarpus sikkimensisFrXXX0.01X0.630.150.640.041.010.080.070.35XXX
Ensete superbumFlXXXXX665.6 ±ramya 5.94518.4 ±ramya 11.063.78 ±ramya 0.15600 ±ramya 4.58180 ±ramya 6.114.46 ±ramya 0.15X176.8 ±ramya 4.8611.74 ±ramya 0.46XX
Enydra fluctuansL, Sh0.980.96X4X24616.990.9480XXXXXX0.096
Euphorbia granulataL, Sh11.683.07X9X42581.091.0124.9XXXXXX0.072
Ficus bengalenisFrXXXXX364XXXXXXXXXX
Ficus geniculataL, Sh0.53XX5X6728.894.6311.3XXXXXX0.012
Ficus racemosaBarkXXXXX172.915.920.0525.51197.50.52X19.620.19XX
Ficus sp.L, Sh8.2XXXX2952.770.87.5XXXXXX0.039
Hibiscus cannabinusL, Sh6.970.070.3920X1722.280.27XXXXXXXX
Ipomoea aquaticaL, Sh1.980.050.1337X1103.9XXXXXXXXX
Kaempferia galangaUXXXXX95069.918.350.3212.230.9160293.9242.650.0012X
Leucas cephalotesL, Sh18.46XX8X23620.020.810.6XXXXXX0.01
Madhuca neriifoliaFr0.307XX40X450.23XXXXXXXXX
Marsilea minutaL, ShXXXXX53XXXXXXXXXX
Meyna spinosaL, ShXXXXX127XXXXXXXXXX
Moringa oleiferaL, Sh6.780.060.05220X4400.850.16XXXXXXXX
Moringa oleiferaFrXXXXX51XXXXXXXXXX
Nelumbo nuciferaSeX0.220.013.940.4644.51.31.33.316301X1655.7XX
Nymphaea nouchaliL, ShXXXXX379.54 ±ramya 0.583.59 ±ramya 0.093.63 ±ramya 0.13643.58 ±ramya 0.82858.39 ±ramya 0.681.77 ±ramya 0.11X145.48 ±ramya 1.11XXX
Nymphaea rubraUXXX14.43 ±ramya 0.03X354.1 ±ramya 01828.14 ±ramya 0.241.64 ±ramya 0.0134.1 ±ramya 0.36734 ±ramya 0.741.12 ±ramya 0.01X104 ±ramya 0.061.34 ±ramya 0.01XX
Oxalis corniculataL, ShXXX21X23414.75XXXXXXXXX
Phyllanthus emblicaFrXXXXX27.63.31.84.2282.00.2828.211.81.10.24X
Polygonum molleFrXXXXX0.150.320.280.092.020.060.270.43XXX
Polygonum plebeiumL, ShXXXXX194XXXXXXXXXX
Portulaca oleraceaL, ShXXX15X22716.17XXXXXXXXX
Prunus cerasoidesFrXXX0.32X0.20.210.20.020.470.010.180.59XXX
Prunus napaulensisFrXXX608.9X122010.71.490.116.51.2270217.746.620.0005X
Quercus roburFrXXXXX4104.71.590.138.31.661501265.630.0002X
Rhus chinensisFrXXXXX10204.172.370.038.410.63160111.1X0.0009X
Schleichera trijugaFrXXXXX15XXXXXXXXXX
Semecarpus anacardiumFrXXXXX2956.1XXXXXXXXX
Senna toraL, Sh10.5120.080.1982X52012.4XXXXXXXXX
Solanum torvumL, Sh0.078XX2.686X22.157.682.14XX0.26XX1.95XX
Spondia pinnataFrXXXXX0.931.32 ±ramya 0.02X1.54 ±ramya 0.011.38 ±ramya 0.801.23 ±ramya 0.030.68 ±ramya 0.01XXXX
Tamarindus indicaFrXXXXX248.56 ±ramya 1.37.14 ±ramya 0.926.94 ±ramya 0.5128.83 ±ramya 1.341315.28 ±ramya 5.740.59 ±ramya 0.16369.47 ±ramya 2.14285.14 ±ramya 2.820.81 ±ramya 0.12XX
Terminalia chebulaFrXXXXX0.810.030.440.081.270.040.040.3XXX
Trianthema portulacastrumL, ShXXX70X10038.5XXXXXXXXX
Urtica dioicaFrXXXXX1.311.31X0.071.87X0.270.42XXX
Viburnum corylifoliumFrXXX238.7X6303.551.620.1111.131.27140161.399.630.0002X
Vicia hirsutaL, Sh0.55XX23X2157.784.1133.18XXXXXX0.07
Zanthoxylum rhetusaFrXXXXX0.880.051.160.020.720.120.140.35XXX
Ziziphus jujubaFr0.210.020.0576X40.50.1XXXXXXXX

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, 207223. 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, 033039.

  • 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, 479487.

  • 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, 222226.

  • 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), 131147. 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, 233236. 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, 541550

  • 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), S12S28. 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, 163168

  • 11

    AyyanarM.IgnacimuthuS. (2005). Traditional knowledge of Kani tribals in Kouthalai of Tirunelveli hills, Tamil Nadu, India. J. Ethnopharmacol.102, 246255. 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, 99105. 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, 868872

  • 14

    BediS. J. (1978). Ethnobotany of the Ratan Mahal Hills, Gujarat, India. Econ. Bot.32, 278284. 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, 305314.

  • 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, 29132926. 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, 111124. 10.1163/1569159054699317

  • 19

    BinuS. (2010). Wild edible plants used by the tribals in Pathanamthitta district, Kerala. Indian J. Tradit. Know.9, 309312

  • 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), 301306.

  • 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, 92101. 10.1016/j.forpol.2016.12.012

  • 22

    CallawayJ. C. (2004). Hempseed as a nutritional resource: an overview. Euphytica140, 6572. 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, 33443349.

  • 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, 1329. 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, 611622.

  • 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), 312. 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, 191197

  • 30

    ChoudharyK.SinghM.PillaiU. (2008). Ethnobotanical survey of Rajasthan-an update. Am. Eurasian J. Bot.1, 3845.

  • 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, 8392. 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), 211215.

  • 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, 397403. 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, 3036.

  • 38

    DeviM. R.SalamS. (2016). Wild edible plants used by the Monsang Naga tribe of Manipur, India. Pleione10, 9096.

  • 39

    DeviO. S.KomorP.DasD. (2010). A checklist of traditional edible bio-resources from Ima markets of Imphal Valley, Manipur, India. J. Threat. Taxa2, 12911296. 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, 151187. 10.1007/BF00889132

  • 41

    DoganY.UguluI.DurkanN. (2013). Wild edible plants sold in the local markets of Izmir, Turkey. Pak. J. Bot.45, 177184.

  • 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), 211215.

  • 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, 103120. 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, 233241. 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, 18.

  • 51

    GhatapanadiS. R.JohnsonN.RajasabA. H. (2011). Documentation of folk knowledge on medicinal plants of Gulbarga district, Karnataka. Indian. J. Tradit. Know.10, 349353.

  • 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, 493519. 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, 548568. 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, 9911006. 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, 2263226810.1182/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, 383414. 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, 155159.

  • 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), 3346.

  • 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, 916. 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, 6669

  • 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, 5157

  • 69

    JainS. K. (1964). Wild plant foods of the tribals of Bastar. Khadi Gramodyog10, 557561.

  • 70

    JeevaS. (2009). Horticultural potential of wild edible fruits used by the Khasi tribes of Meghalaya. J. Hortic. For. 1, 182192.

  • 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, S20S25. 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, 76978210.1093/nutrit/nux040

  • 73

    KarA. (2004). Common wild vegetables of Aka tribe of Arunachal Pradesh. Indian J. Trad. Know.3, 305313

  • 74

    KarA.BorthakurS. K. (2007). Wild vegetables sold in local markets of Karbi Anglong, Assam. Indian J. Tradit. Know.6, 169172

  • 75

    KarA.BorthakurS. K. (2008). Wild vegetables of Karbi-anglong district, Assam. Nat. Prod. Rad.7, 448460

  • 76

    KatewaS. S.ChaudharyB. L.JainA.GalavP. (2003). Traditional uses of plant biodiversity from Aravalli hills of Rajasthan. Indian J. Tradit. Knowl.2, 2739

  • 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, 28329310.5586/asbp.2012.048

  • 78

    KhanT. M.KakdeU. B. (2014). Biodiversity in wild vegetables of Konkan region - Maharashtra. Int. J. Res. Biosci. Agric. Technol.2, 226240.

  • 79

    KhaundP.JoshiS. R. (2013). Wild edible macrofungal species consumed by the Khasi tribe of Meghalaya, India. Indian J. Nat. Prod. Res.4, 197204.

  • 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, 760766. 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, 9095

  • 83

    KumarV.JainS. K. (2002). Plant products in some tribal markets of central India. Econ. Bot.56, 242245. 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, 119121. 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, 130142. 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, 218230. 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, 23124110.1016/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, 245255. 10.5586/asbp.2012.030

  • 90

    LykkeA. M.MertzO.GanabaS. (2002). Food consumption in rural Burkina Faso. Ecol. Food Nutr.41, 119153. 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, 468472.

  • 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, 219234. 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, 5668. 10.1080/13504509409469861

  • 95

    ManiM. S. (1974). Biogeographical evolution in India, in Ecology and Biogeography in India, ed ManiM. S. (Dordrecht: Springer), 698724. 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, 96103.

  • 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, 6679.

  • 99

    MedhiP.SarmaA.BorthakurS. K. (2014). Wild edible plants from the Dima Hasao district of Assam, India. Pleione8, 133148.

  • 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, 1467414679. 10.1073/pnas.1607872113

  • 101

    MishraM.ShrivastavaM. (2015). Trade of minor forest products in the rural markets of central India. Biol. Forum7, 516521.

  • 102

    MishraM. L.SoodS.ShuklaU. N. (2018). Phyto-nutritional and mineral composition of Indian horse chestnut (Aesculus indica) seeds. J. Pharm. Phytochem.7, 21592162. 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, 8289.

  • 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), 117.

  • 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, 20332054. 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, 122. 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, 6974.

  • 109

    MohanV. R.KalidassC. (2010). Nutritional and antinutritional evaluation of some unconventional wild edible plants. Trop. Subtrop. Agroecosyst.12, 495506.

  • 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, 303308.

  • 112

    NairR.AgrawalV. (2017). Nutritive values and uses of some important arid zone fruit trees of Madhya Pradesh. Int. J. Chem. Stud.5, 399404.

  • 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, 35203529.

  • 115

    NathA.MaitiG. G. (2011). An ethnobotancial report on less-known leafy vegetables consumed by different communities of Barak valley, Assam, India. Ecobios4, 4555.

  • 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, 398402

  • 118

    NeogiB.PrasadM. N.RaoR. R. (1989). Ethnobotany of some weeds of Khasi and Garo hills, Meghalaya, Northeastern India. Econ. Bot. 43, 471479. 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, 130. 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, 4164. 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, 103117. 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, 144146.

  • 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, B144B159

  • 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, 12771289.

  • 128

    PandeyA. K.BoraH. R. (1997). Edible plants of Shan tribe of Assam. Anc. Sci. Life16, 258276

  • 129

    PandeyG. (1998). Wild temperate fruit plants of Himachal Pradesh, India. Plant Genet. Resour. Newslett.116, 911.

  • 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, 80881810.12944/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, 185190

  • 132

    PantS.SamantS. S. (2010). Ethnobotanical observations in the Mornaula reserve forest of Komoun, West Himalaya, India. Ethnobot. Leaflets14, 193217

  • 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, 3750

  • 135

    ParisaraN.KiranB. R. (2016). Enumeration of leafy vegetables of BhadravathiTaluk, Karnataka. Int. J. Sci. Res. Sci. Technol.2, 3235.

  • 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, 108131. 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, 5770. 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, 5062.

  • 140

    PingaliP. (2015). Agricultural policy and nutrition outcomes – getting beyond the pre-occupation with staple grains. Food Secur.7, 583591. 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, 187198. 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, 535554. 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), 65100.

  • 146

    PugalenthiM.VadivelV.GurumoorthiP.JanardhananK. (2004). Comparative nutritional evaluation of little known legumes, Tamarindus indica, Erythrina indica and Sesbania bispinosa. Trop. Subtrop. Agroecosyst.4, 107123.

  • 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, 6573.

  • 148

    RajasabA. H.IsaqM. (2004). Documentation of folk knowledge on edible wild plants of North Karnataka. Indian J. Tradit. Know.3, 419429.

  • 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, 225238. 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, 173176

  • 151

    RamachandranV. S.JosephS.ArunaR. (2009). Ethnobotanical studies from Amaravathy range of Indira Gandhi wildlife sanctuary, Western Ghats, Coimbatore District, Southern India. Ethnobot. Leaflets13, 10691087.

  • 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, 135149. 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, 297306. 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, S1493S1497. 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, 103108.

  • 156

    RowlandD.IckowitzA.PowellB.NasiR.SunderlandT. C. H. (2016). Forest foods and healthy diets: quantifying the contributions. Environ. Conserv.44, 102114. 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, 432437

  • 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, 198201.

  • 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, 8287.

  • 161

    SasiR.RajendranA.MaharajanM. (2011). Wild edible plant diversity of Kotagiri hills - a part of Nilgiri biosphere reserve, Southern India. J. Res. Biol.2, 8087.

  • 162

    SathyavathiR.JanardhananK. (2014). Wild edible fruits used by Badagas of Nilgiri district, Western Ghats, Tamilnadu, India. J. Med. Plants Res.8, 128132. 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, 125131. 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, 17

  • 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, 227229. 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, 263277. 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, 425431.

  • 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. 217232.

  • 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, 4756.

  • 173

    SinghV. N.ChanuL. I.BaruahM. K. (2011). An ethnobotanical study of Chirus-A less known tribe of Assam. Indian J. Tradit. Know.10, 572574.

  • 174

    SinhaR.LakraV. (2005). Wild tribal food plants of Orissa. Indian J. Tradit. Know.4, 246252

  • 175

    SinhaR.LakraV. (2007). Edible weeds of tribals of Jharkhand, Orissa and West Bengal. Indian J. Tradit. Know. 6, 217222

  • 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, 97197610.1080/11263504.2014.994577

  • 178

    SundriyalM.SundriyalD. C. (2001). Wild edible plants of the Sikkim himalaya: nutritive values of selected species. Econ. Bot.55, 37739010.1007/BF02866561

  • 179

    SundriyalM.SundriyalR. C. (2003). Underutilized edible plants of the Sikkim himalaya: need for domestication. Curr. Sci.25, 731736.

  • 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, 86100.

  • 181

    SwarnkarS.KatewaS. S. (2008). Ethnobotanical observation on tuberous plants from tribal area of Rajasthan (India). Ethnobot. Leaflets12, 647666. 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, 2771. 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, 4056.

  • 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, 167174.

  • 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, 198225. 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), 157196.

  • 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, 499509. 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, 948953.

  • 190

    VishwakarmaK. L.DubeyV. (2011). Nutritional analysis of wild edible herbs used in eastern Chhattisgarh, India. Emir. J. Food Agric.15, 554560.

  • 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, 11371142. 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): S29S42. 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, 514529.

  • 197

    YuhlungC. C.BhattacharyyaM. (2014). Practice of ethno-medicine among the Chothe tribe of Manipur, North-East India. Int. J. Pharm. Biol. Arch.5, 138149.

  • 198

    YumnamJ. Y.BhuyanS. I.KhanM. L.TripathiO. P. (2011). Agro-diversity of East Siang-Arunachal Pradesh, Eastern Himalaya. Asian J. Agric. Sci.3, 317326.

  • 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, 321334. 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

*Correspondence: Avik Ray

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.

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