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Article

Nutrient and Mineral Compositions of Wild Leafy Vegetables of the Karen and Lawa Communities in Thailand

by
Kittiyut Punchay
1,
Angkhana Inta
1,
Pimonrat Tiansawat
1,
Henrik Balslev
2 and
Prasit Wangpakapattanawong
1,3,*
1
Department of Biology, Faculty of Science, Chiang Mai University, Huay Kaew Road, Chiang Mai 50200, Thailand
2
Ecoinformatics and Biodiversity Group, Department of Biology, Aarhus University, Building1540, NyMunkegade114-116, DK-8000 Aarhus C, Denmark
3
Environmental Science Research Center (ESRC), Faculty of Science, Chiang Mai University, Huay Kaew Road, Chiang Mai 50200, Thailand
*
Author to whom correspondence should be addressed.
Foods 2020, 9(12), 1748; https://doi.org/10.3390/foods9121748
Submission received: 19 October 2020 / Revised: 19 November 2020 / Accepted: 24 November 2020 / Published: 26 November 2020
(This article belongs to the Section Food Security and Sustainability)

Abstract

:
Wild food plants are commonly used in the traditional diets of indigenous people in many parts of the world, including northern Thailand. The potential contribution of wild food plants to the nutrition of the Karen and Lawa communities remains poorly understood. Wild food plants, with a focus on leafy vegetables, were ranked by the Cultural Food Significance Index (CFSI) based on semi-structured interviews. Twelve wild plant species were highly mentioned and widely consumed. The importance of the wild vegetables was mainly related to taste, availability, and multifunctionality of the species. Their contents of proximate and minerals (P, K, Na, Ca, Mg, Fe, Mn, Zn, and Cu) were analyzed using standard methods. The proximate contents were comparable to most domesticated vegetables. The contents of Mg (104 mg/100 g FW), Fe (11 mg/100 g FW), and Zn (19 mg/100 g FW) in the wild leafy vegetables were high enough to cover the daily recommended dietary allowances of adults (19–50 years), whereas a few species showed Mn contents higher than the tolerable upper intake level ( > 11 mg/100 g edible part). The wild leafy vegetables, therefore, are good sources of minerals and we recommend their continued usage by indigenous people. Further research on these wild leafy vegetables’ contents of antioxidants, vitamins, heavy metals, anti-nutrient factors, and food safety is recommended.

1. Introduction

The consumption of wild plants persists in many communities, especially among indigenous peoples to whom wild food plants are part of their traditional food systems [1]. Indigenous people often experience food insecurity and malnutrition, but local communities often possess traditional knowledge that can help them to alleviate these problems through harvesting, hunting, and gathering of wild plants [2,3]. Of the 380,000 different vascular plants known globally [4,5], only nine species represent two thirds (66%) of all the crop production. These nine species are maize (Zea mays), rice (Oryza sativa), wheat (Triticum aestivum), potato (Solanum tuberosum), soybean (Glycine max), oil palm (Elaeis guineensis), cassava (Manihot esculenta), sugar cane (Saccharum officinarum), and sugar beet (Beta vulgaris) [2]. In comparison, the importance of wild plants as a source of nutrients and minerals has been documented in many studies which show that they may cover required dietary intakes [6,7,8,9,10,11,12,13,14]. Moreover, wild plants not only have important roles in diets, but some of them also provide important health benefits with documented biological and pharmacological effects [10,15,16,17]. Therefore, renewed attention to wild plants, documenting their value, may increase food and health security in traditional communities.
Thailand has a high diversity of ethnicities, especially in the highlands in the north. The Karen are the largest ethnic group inhabiting the mountainous areas of northern Thailand [18]. The Lawa, in contrast, are one of the smallest ethnic groups, and they live scattered over northern Thailand [19]. The rotational swidden rice-based agricultural systems of the Karen and the Lawa have maintained many useful plants in microenvironments between their agricultural fields [20], and, in addition, they use a large number of forest plants for food, construction, fuel, medicine, animal food, clothes, and ritual purposes [21].
Many ethnobotanical studies from northern Thailand [20,21,22,23,24,25,26,27,28,29,30,31,32,33,34,35,36,37,38] describe a rich traditional knowledge which includes over 1700 plant species [39]. However, the research has not pinpointed the plant species that provide the daily dietary intake of these indigenous people. Still, the ethnic minorities in northern Thailand face food insecurity and malnutrition [40,41,42,43]. Promoting the consumption of traditional diets could improve nutrition because a number of wild food species, in particular ones that are used as vegetables, have been reported to have high nutritional qualities that surpass conventional vegetables [10,14,44,45]. However, the information on the nutritional composition of wild leafy vegetable species in Thailand is limited and incomplete. Knowledge of nutrition- or health benefits may improve the perception of and attitude toward wild food plants [46]. The nutrient composition of wild food plants may provide informative data that will be advantageous to the health- and food security not only for indigenous people but also the rest of the population.
Malnutrition is one of the challenges of public health when it comes to sustainable development goals (SDGs) in many developing countries [47]. Malnutrition increases the risk of chronic diseases, stunting, and, eventually, nutritional disorder. Furthermore, the deficiency of minerals, i.e., calcium and zinc, is recognized as a health problem worldwide based on food supply [48,49]. In Thailand, the number of under-nourished people between 2016 and 2018 was five million, whereas the prevalence of stunting children was ten percent, and five percent of wasting in the total population [3]. Most ethnic minorities experience mineral deficiency in their diets [40,41,43,50,51].
In this study, based on the food knowledge of the Karen and the Lawa, we determined the cultural food significance of wild leafy vegetable species for nutritional analysis. Nutrient compositions, which included proximate analyses (moisture, ash, protein, fat, fiber, and carbohydrate), and minerals composition (P, K, Ca, Mg, Fe, Na, Mn, Zn, and Cu), were evaluated. Nutrient composition data from our study should help in expanding nutrient databases and are beneficial for future research on food and human health.

2. Materials and Methods

2.1. Selection of Wild Leafy Vegetable Species

For this study, we used the Cultural Food Significance Index (CFSI) to evaluate the cultural significance of wild leafy vegetable species. The CFSI, developed by Pieroni in 2001 [52], is the sum of seven measures of food importance and is calculated as:
CFSI = QI × AI × FUI × PUI × MFFI × TSAI × FMRI × 10−2
where QI = quotation index; AI = availability index; FUI = frequency of utilization index; PUI = plant parts used index; MFFI = multi-functional food use index; TSAI = taste score appreciation index; and FMRI = food-medicinal role index [52,53]. To determine the QI, the number quotation of each useful species for particular use was counted. The interviewees were asked “How many of these vegetables can be found in the forest?” to determine the AI with the following categories: rare, medium, common, and very common. The FUI values were determined by asking about the frequency of eating these species. The PUI values express the multiple uses of a plant part. If multiple parts were collected, the value will be higher than the use of single plant part. The MFFI values were obtained by asking interviewees “How do you consume this vegetable?” High values were allocated to raw consumption or cooked alone species, and low values were obtained by using with other ingredients or condiments. The TSAI values were assessed by asking how much interviewees like these vegetables on the following scale: terrible, poor, fair, good, very good, and best. Some vegetable species had medicinal benefits in different roles. High values of FMRI were allocated with food as medicine, while low values were obtained from species that had no specification of therapeutic action, or where it was not recognized. All sub-indices were evaluated using Pieroni’s scales [52]. Wild leafy vegetable species with CFSI ≥ 300 in the Karen and Lawa communities were selected to analyze the proximate and mineral components.

2.2. Study Sites

Two Karen and two Lawa villages in Mae Chaem District, Chiang Mai, Thailand, were selected. This area is rich plant diversity, and local people traditionally gather wild food plants [29]. Wild vegetable species naturally grow in lower montane rainforest and fallows. The elevations range from 700 to 1100 m above sea level. The Cultural Food Significance Index (CFSI) was determined for the wild food plant species through semi-structured interviews with 48 Karen and 53 Lawa villagers (age range 20–85 years) in 2018 [29]. All procedures performed were in accordance with the International Guidelines for Human Research Protection and the International Society of Ethnobiology (ISE) Code of Ethics [54]. Informed consent was obtained from all participants. Ethical approval was obtained from the Chiang Mai University Research Ethic Committee (certificate of approval no. 019/61). Wild leafy vegetables were collected in the fields with the assistance of the informants and identified by the first author. All voucher specimens were deposited at the Department of Biology, Chiang Mai University Herbarium (CMUB) [29].

2.3. Preparation of Samples

For analysis, one kilogram of each plant species was sampled in the study villages from July to December 2019. The most-used plant part of each wild leafy vegetable species was selected for analysis. The homogenized samples were subsampled. After that, the fresh materials were rinsed and cleansed with deionized water. Only edible parts were kept and the excess deionized water was dried off at room temperature. Wild vegetable parts were packed in zip-lock bags. The analyses were performed at the Agricultural Technology Service Center, Chiang Mai University, on the day after collecting the vegetables. The scientific nomenclature of the plants used follow the World Flora Online [55]. The distribution and occurrence of all the plant species were retrieved from the Global Biodiversity Information Facility (GBIF, www.gbif.org).

2.4. Chemical Analyses

Analyses of moisture content, ash, macrominerals, and trace minerals were carried out using standard methods of analysis of the Association of Official Agricultural Chemists (AOAC) [56] and reference methods for plant analysis [57]. Moisture content was measured following method 930.15 [56]. The plant samples were dried in a hot air oven at 135 °C for 2 h. The weights of the dried samples were measured and expressed as percentages of the moisture content. Ash content was determined following method 942.05 [56]. The samples were put into a crucible and placed in a temperature control furnace at 600 °C for two hours. The ash content was obtained by measuring the weight. Total protein was determined via nitrogen content by the combustion technique (LECO model FP-828) with a conversion factor of 6.25, following method 968.06 [56].
Crude fat extraction was determined using a Soxhlet apparatus and petroleum ether. Crude fat residues were measured after drying, following method 954.02 [56]. The crude fiber was estimated by the gravimetric method; the material was digested with sulfuric acid and sodium hydroxide solution, following method 962.09 [56]. Total carbohydrate was obtained by subtracting the value of water, crude protein, crude fiber, ash, and fat from 100, following method 991.43 [56,58]. Mineral elements analyses (phosphorus, potassium, sodium calcium, magnesium, iron, manganese, zinc, and copper) were performed using atomic absorption spectroscopy (Analytik Jena, model ZEEnit 700). About 1 g of dry ash of a sample was wetted with a small volume of deionized water and then brought into a solution using 2 mL of HCl. For determination of potassium, calcium, and magnesium, the final volume should be 100 mL, which is sufficiently above the detection limit for a 1.0-g sample. For determination of manganese, iron, copper, and zinc, the final volumes should be between 10 and 50 mL. Quantification of each element was performed using atomic absorption spectrometry and comparing the linear curve from the standard solution with the sample [57]. All analyses were carried out in triplicate.

2.5. Data Analysis

All sub-indices of CFSI were calculated by Microsoft Excel to indicate the cultural significance of the species. To determine the reason for the use of wild leafy vegetables, values of all sub-indices were given the same weight. The relationship between quotations and sub-indices were illustrated by Chord diagram in the R programming language. Each value from the nutrient analyses was obtained by calculating the average of three measurements, and data are presented as mean ± SD. The comparison of the means of minerals was determined by Tukey’s test and statistical significance was accepted at the p < 0.05 level. Nutrient contents are reported per 100 g of fresh weight compared to The Essential Guide to Nutrient Requirements by the National Academy of Sciences and the Dietary Reference Intake for Thais [59,60].

3. Results

3.1. Cultural Food Significance Index (CFSI)

According to the Cultural Food Significance Index, twelve wild food species had high CFSI values in both the Karen and the Lawa villages (Table 1). The folk names and traditional uses by the Karen and the Lawa of wild leafy vegetables are provided in Table 1. Most of the leafy vegetables originated in Asia, but a few species were more widely distributed, i.e., Centella asiatica, Acmella uliginosa, and Musa acuminata. The taste of the plant, the availability of plants, and multiple functionality were the main drivers of high significance, whereas the frequency of use, plant parts used, and medicinal roles were less important (Figure 1). The highest taste score was for Oroxylum indicum (15%), followed by Spondias pinnata (10%) and Ficus auriculata (9%). Most informants mentioned that the twelve wild leafy vegetables are very common and easy to collect and are available for a long collection period (Table 1). The multiple food uses of the twelve leafy vegetable species were cooked as soup (33%), eaten raw (31%), and boiled (10%). Most of the informants mentioned that the frequency of the leafy vegetable use was one time each month (36%), one time each week (21%), and more than one time each year but less than once per month (18%), respectively. The food medicinal role index values for the twelve wild leafy vegetables were smaller than their values for other sub-indices because the informants did not recognize the twelve wild vegetable species except Centella asiatica, which received a very high score.

3.2. Nutritional Properties

The proximate compositions of the twelve wild leafy vegetable species on a wet basis vary considerably (Table 2). Their moisture contents were in the range of 62.9–95.3 g/100 g fresh weight (FW). The lowest value was found in Lygodium flexuosum and the highest was for Musa acuminata, from which we sampled the fleshy inner pseudostem. The ash contents ranged from 0.79 to 4.28 g/100 g FW. The lowest ash content was obtained from Oroxylum indicum and Senegalia rugata and the highest was in Spondias pinnata. The protein contents ranged from 0.48 to 5.33 g/100 g FW. The highest protein content was observed in Clerodendum glandulosum, whereas the lowest protein content was observed in Musa acuminata. The fat contents ranged from 0.10 to 0.78 g/100 g FW, with the lowest in M. acuminata and the highest in L. flexuosum. The highest fiber content was found in the leaves of Lygodium flexuosum (11.82 g/100 g FW), while the lowest fiber content was observed in Monochoria vaginalis (0.79 g/100 g FW). The carbohydrate contents ranged from 1.54 to 17.94 g/100 g FW. The lowest carbohydrate content was found in M. acuminata and the highest was in L. flexuosum.

3.3. Minerals Content

The contents of macrominerals (P, K, Mg, Ca, and Na) and trace minerals (Fe, Cu, Zn, and Mn) in the selected wild leafy vegetable species vary widely among the species (Table 3). The potassium content was the highest in all the studied species and ranged from 221.7 to 1291.3 mg/100 g FW in Senegalia rugata and Oenanthe javanica, respectively. The calcium content was the second highest in leafy vegetables and ranged from 2.6 to 982.9 mg/100 g FW. The phosphorus content of the wild vegetables ranged from 9.3 to 77.7 mg/100 g FW. The highest phosphorus content was found in Senegalia rugata, while the lowest was observed in Musa acuminata. The magnesium content ranged from 6.0 to 104.4 mg/100 g FW. The highest magnesium content was obtained from Centella asiatica, while the lowest magnesium content was found in Spondias pinnata. The sodium content ranged from 0.4 to 21.2 mg/100 g FW, with the highest content obtained from Centella asiatica and the lowest content from Musa acuminata. The iron contents ranged from 0.3 to 11.1 mg/100 g. The highest iron content was found in Acmella paniculata, whereas the lowest content was observed in Oroxylum indicum. The manganese contents varied from 0.2 to 15.7 mg/100 g. Moreover, the copper content was the lowest in all the plant species. Monochoria vaginalis and Musa acuminata had copper contents below 0.01 mg/100 g fresh weight, while the highest copper content was found in Oroxylum indicum (0.41 mg/100 g FW).

4. Discussion

4.1. Cultural Food Significance Index

The wild leafy vegetable species had high CFSI values in both the Karen and the Lawa communities and these values were similar to those found for wild food plants in northwestern Tuscany, Italy [52]. They were, however, not as high as the values found for edible fruits and seeds in Bali, Indonesia, probably because the fruit species had multiple uses, including for medicine [53]. Time may influence the selection of wild food because fruits are more difficult to harvest than leafy vegetables. Besides, most wild leafy vegetables with high CFSI values had medicinal properties in both the Karen and Lawa communities (Table 1), which increased the sub-element of the CFSI scores [52,53,61,62]. Moreover, the availability of vegetables and the multifunctionality of food uses, i.e., fresh consumption, food addition, and condiment, are related to highly important species [52]. Using a compound index is a powerful tool to understand the cultural significance of resources in more detail, but informants have to deal with a large number of questions for every sub-element for each species known, and that is very time consuming [61]. The reasons for using wild leafy vegetables were mainly related to taste, availability, and multifunctionality, which is similar to trends in the use of wild vegetables in West Sumatra, Indonesia [46]. Taste is a sociocultural factor for wild food plant consumption which appears to be a prime motivation for continuing consumption of wild food plants [63], and this is related to changes in the use of wild food plants [64]. Moreover, loss of availability of familiar food taxa from the wild is one of the main reasons for a decrease in wild food plant consumption [64].

4.2. Proximate Composition

The moisture content of the 12 species studied fluctuated from 60 to 90%, which is usual in leafy vegetables [65,66,67,68]. The high moisture content reveals that leafy vegetables need appropriate preservation because they are likely to degrade by microbial activity [69]. The range of the ash contents was similar to that of wild vegetables in the western Himalayas [70] and India [71]. Besides, ash content indicates an excellent source of the mineral element in vegetables [13], because ash contains inorganic materials, including anions, cations, oxides, and salts [72]. The range of fiber contents was similar to wild food plants in India [71] but lower than wild food plants in Bangladesh [11]. The fiber contents of Centella asiatica, Clerodendrum glandulosum, and Oenanthe javanica (Table 2) were similar to fiber contents of domesticated leafy vegetables, i.e., Chinese cabbage (2.2 g/100 g FW), celery (1.6 g/100 g FW), and coriander (2.8 g/100 g FW) [73]. High fiber content has significant benefits for the digestive system, including regulation of intestinal function, glucose tolerance, and prevention of chronic diseases, such as colon cancer [74,75]. However, an excess of fiber causes a negative effect on mineral absorption of, for instance, iron [76]. The protein contents were comparable to other indigenous vegetables in India [68,70] and Thailand [12,67]. The protein contents of C. gladulosum and Senegalia rugata (Table 2) were higher than that of kale (Brassica oleracea), whose protein content was 4.28 g/100 g for the edible portion [73]. However, the protein contents were low when compared with the Dietary Reference Intake for Thai adults (0.9‒8.6% recommended per day) [60]. The content of fat in leafy vegetables were commonly reported to be from <1‒3 g/100 g [7,9,10,11,12,14]. The fat contents in the wild food plants in this study were all lower than 1%, similar to the edible flowers of Zingiberaceae in Thailand [67] and domesticated leafy vegetables, i.e., asparagus (0.1 g/100 g FW), lettuce (0.2 g/100 g FW), and spinach (0.4 g/100 g FW) [73]. Fats are involved in many vital processes in the body, such as the absorption of fat-soluble vitamins [77], which may be correlated with deficiency of fat, vitamin A, and vitamin E among children of the ethnic minorities in northern Thailand [42,43]. The average carbohydrate content was similar to values obtained for indigenous vegetables in southern Thailand [12]. Some wild vegetables, i.e., Oroxylum indicum, Clerodendum glandulosum, and Centella asiatica, have carbohydrate values that are higher than cultivated vegetables, such as cabbage (3.2 g/100 g FW) or carrot (4.9 g/100 g FW) [78], which contributed to the nutrition, food security, and health by substitute for resource-poor farmers in developing regions [10].

4.3. Mineral Content

Minerals are important in the physiological processes of the human body. Sodium and potassium function as electrolytes, which maintain ionic balance and establish the electric potential across cellular membranes [59,72]. According to the nutrient composition database of food made available by United States Department of Agriculture (USDA), many wild leafy vegetables show high contents of macrominerals and trace minerals when compared with domesticated leafy vegetables. The range of the sodium content in the 12 species studied here was quite low when compared with the recommended dietary intake for adults (0.02‒1.4% recommended per day) (Table 4) [59]. Low sodium contents in wild vegetables have been reported in previous studies of wild vegetables [70,72,79] and domesticated leafy vegetable, i.e., asparagus (2 mg/100 g), lettuce (5 mg/100 g), and Chinese cabbage (29 mg/100 g) [73]. In our data, the potassium contents were higher than what was found in indigenous vegetables in southern Thailand [12], and some species have moderate potassium levels (5‒27% of RDA) when compared with recommended dietary intakes. The calcium contents varied, but some species, such as Spondias pinnata and Ficus auriculata, had higher calcium levels in fresh weight than wild edible plants in Bangladesh [77,80]. Wild Asteraceae members in this study were high in calcium, similar to wild Asteraceae in traditional Mediterranean diets [14]. The contribution of leafy vegetables to calcium content showed the highest percentage in Spondias pinnata (98% of RDA). The calcium content of S. pinnata was six times higher than the calcium contents of Chinese cabbage (150 mg/100 g FW) and kale (152 mg/100 g FW) [73].
The consumption of wild plants, for instance, Centella asiatica (31–41% of RDA) and Clerodendrum glandulosum (21–27% of RDA) (Table 4), can help villagers to meet the recommended magnesium intake, which prevents gastrointestinal disorders, renal loss, endocrine and metabolic disorder, cutaneous loss, and redistribution of magnesium to the bones [59]. The iron contents in the wild vegetables were high and similar to leafy vegetables in Africa [13], India [70,72], and Bangladesh [77]. The contribution of leafy vegetables to improving iron intake is relatively high in terms of percentage of recommended dietary allowances, i.e., Acmella paniculata (61–138% of RDA), A. uliginosa (59–133% of RDA), Monochoria vaginalis (51–116% of RDA), and Oenanthe javanica (38–87% of RDA) (Table 4). According to the daily iron takes of Thai children, the range of iron intake is between 6.6 and 8.4 mg/day [49], whereas the recommended dietary allowance in children is 7–11 mg/day [59]. This causes Fe deficiency in Thai children in urban (32%) and rural (38%) areas [49]. However, it would take 50–100 g (fresh weight) of iron-rich species to reach the recommended volume, and the consumption of iron-rich species should be a food of choice for Thai children suffering from anemia caused by Fe deficiency. The copper levels of Acmella species were similar to the wild Asteraceae in Mediterranean countries, which were reported to be 0.01‒0.4 mg/100 g [14].
Interestingly, the manganese content was relatively high, surpassing the daily requirement for adults [60]. Manganese is a natural part of most foods [81]. Although manganese is essential to bone structure, metabolism, and function as a powerful antioxidant, a high level of manganese can cause harm to the nervous system, which, in turn, may cause insomnia, depression, or illusions and, eventually, progressive alterations in gait and balance and tremor and Parkinson-like symptoms [82]. According to the percentage of recommended dietary allowance of manganese, many wild leafy vegetables show a very high percentage, such as Centella asiatica, Monochoria vaginalis, and Lygodium flexuosum, while the manganese contents of domesticated leafy vegetables, i.e., asparagus, Chinese cabbage, celery, lettuce, spinach, and kale, show less than one milligram per 100 g fresh weight [73]. However, the consumption of manganese-rich species should be cautioned regarding tolerable upper intake level of manganese, but the risk of excess intake of manganese from food appears to be low [59]. Furthermore, the Department of Mineral Resources considered our study villages in Mae Chaem district as having manganese mineral deposits [83]. Zinc was found in high levels when compared with previous studies of wild plants [11,14,72,79]. A study of dietary intakes of 0.5–12-year-old Thai children indicated that more than 50% of urban and rural Thai children have a low intake of zinc—only 4 mg/day [49]—whereas the dietary reference intake of Thai children (0.5–12-year-old) ranged from 2.7 to 9.5 mg/day [60]. The consumption of a high percentage of zinc as per the RDA, i.e., Centella asiatica, Oenanthe javanica, and Clerodendum glandulosum, could prevent Thai children from the risks of chronic diseases, such as growth retardation, eye and skin lesions, and delayed sexual maturation and impotence [59].

5. Conclusions

Our study has revealed the importance of wild food plant species, particularly leafy vegetables, commonly used in traditional diets in northern Thailand. The importance of wild vegetables was mainly related to taste, availability, and multifunctionality of species, whereas the frequency of utilization, plant parts, and medicinal roles are less important. The proximate compositions are comparable with most domesticated leafy vegetables. It illustrates the potential of wild plants as sources of essential nutrients. These wild vegetables are rich in macrominerals and trace minerals when compared with recommended dietary allowances, including magnesium (41% of RDA), iron (138% of RDA), and zinc (242% of RDA). A few wild vegetable species showed high manganese contents that exceeded tolerable upper intake level ( > 11 mg/100 g edible parts), producing health risks. The data have been mostly quantitative with fresh leafy vegetables. This is important and underlines the need to pay attention to the quantity of wild plant selection and consumption. The determination of bioavailability of minerals, antioxidants, vitamins, heavy metals, and anti-nutrient factors from these wild plants is necessary to evaluate their safety. Pharmacological studies should also be conducted to verify some of the ethnomedicinal properties.

Author Contributions

Conceptualization, K.P. and P.W.; experimental design, K.P., A.I., P.T., H.B., and P.W.; sample collection, K.P.; data curation, K.P.; writing—original draft preparation, K.P.; writing—review and editing, A.I., P.T., H.B., and P.W.; supervision, P.W.; project administration, K.P. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Royal Golden Jubilee Program (RGJ) of the Thailand Research Fund, grant number PHD/0080/2557, This research was partially supported by Chiang Mai University; H.B. acknowledges support from the Carlsberg Foundation (CF14-0245) to study the Thai flora.

Acknowledgments

We are especially grateful to the people of the Din Kao, Mae Tum, Ho, and Kok Noi villages for generous help and for sharing their knowledge about the use of wild leafy vegetables. We are also grateful to the staff of Ethnobotany and Northern Thai Flora, Department of Biology, Chiang Mai University, for assistance and facilities during the field survey. We also thank valuable comments from reviewers, which helped improve the quality of the manuscript.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

References

  1. Kuhnlein, H.V.; Erasmus, B.; Spigelski, D. Indigenous Peoples’ Food Systems: The Many Dimensions of Culture, Diversity and Environment for Nutrition and Health; Food and Agriculture Organization of the United Nations: Rome, Italy, 2009. [Google Scholar]
  2. FAO. The State of the World’s Biodiversity for Food and Agriculture; Food and Agriculture Organization of the United Nations: Rome, Italy, 2019.
  3. FAO; IFAD; UNICEF; WFP; WHO. The State of Food Security and Nutrition in the World 2018 Building Climate Resilience for Food Security and Nutrition; Food and Agriculture Organization of the United Nations: Rome, Italy, 2018.
  4. RBG Kew. State of the World’s Plants 2016; Royal Botanic Gardens, Kew: Richmond, UK, 2016. [Google Scholar]
  5. Willis, K.J. State of the World’s Plants 2017; Royal Botanic Gardens, Kew: Richmond, UK, 2017. [Google Scholar]
  6. Jones, A.M.P.; Ragone, D.; Aiona, K.; Lane, W.A.; Murch, S.J. Nutritional and morphological diversity of breadfruit (Artocarpus, Moraceae): Identification of elite cultivars for food security. J. Food Compos. Anal. 2011, 24, 1091–1102. [Google Scholar] [CrossRef]
  7. Nkafamiya, I.; Osemeahon, S.; Modibbo, U.; Aminu, A. Nutritional status of non-conventional leafy vegetables, Ficus asperifolia and Ficus sycomorus. Afr. J. Food Sci. 2010, 4, 104–108. [Google Scholar]
  8. Salehi, M.; Kuhnlein, H.V.; Shahbazi, M.; Kimiagar, M.S.; Kolahi, A.A.; Mehrabi, Y. Effect of traditional food on nutrition improvement of Iranian tribeswomen. Ecol. Food Nutr. 2005, 44, 81–95. [Google Scholar] [CrossRef]
  9. Seal, T. Evaluation of nutritional potential of wild edible plants, traditionally used by the tribal people of Meghalaya state in India. Am. J. Plant Nutr Fertil. Technol. 2012, 2, 19–26. [Google Scholar] [CrossRef] [Green Version]
  10. Singh, A.; Dubey, P.K.; Chaurasiya, R.; Mathur, N.; Kumar, G.; Bharati, S.; Abhilash, P.C. Indian spinach: An underutilized perennial leafy vegetable for nutritional security in developing world. Energy Ecol. Environ. 2018, 3, 195–205. [Google Scholar] [CrossRef]
  11. Alam, M.K.; Rana, Z.H.; Islam, S.N.; Akhtaruzzaman, M. Comparative assessment of nutritional composition, polyphenol profile, antidiabetic and antioxidative properties of selected edible wild plant species of Bangladesh. Food Chem. 2020, 320, 126646. [Google Scholar] [CrossRef]
  12. Kongkachuichai, R.; Charoensiri, R.; Yakoh, K.; Kringkasemsee, A.; Insung, P. Nutrients value and antioxidant content of indigenous vegetables from Southern Thailand. Food Chem. 2015, 173, 838–846. [Google Scholar] [CrossRef]
  13. Ntuli, N.R. Nutrient content of scarcely known wild leafy vegetables from northern KwaZulu-Natal, South Africa. S. Afr. J. Bot. 2019, 127, 19–24. [Google Scholar] [CrossRef]
  14. García-Herrera, P.; Sánchez-Mata, M.C.; Cámara, M.; Fernández-Ruiz, V.; Díez-Marqués, C.; Molina, M.; Tardío, J. Nutrient composition of six wild edible Mediterranean Asteraceae plants of dietary interest. J. Food Compos. Anal. 2014, 34, 163–170. [Google Scholar] [CrossRef]
  15. Baliga, M.S.; Shivashankara, A.R.; Haniadka, R.; Dsouza, J.; Bhat, H.P. Phytochemistry, nutritional and pharmacological properties of Artocarpus heterophyllus Lam. (jackfruit): A review. Food Res. Int. 2011, 44, 1800–1811. [Google Scholar] [CrossRef]
  16. Patel, J.J.; Acharya, S.R.; Acharya, N.S. Clerodendrum serratum (L.) Moon—A review on traditional uses, phytochemistry and pharmacological activities. J. Ethnopharmacol. 2014, 154, 268–285. [Google Scholar] [CrossRef] [PubMed]
  17. Pranskuniene, Z.; Dauliute, R.; Pranskunas, A.; Bernatoniene, J. Ethnopharmaceutical knowledge in Samogitia region of Lithuania: Where old traditions overlap with modern medicine. J. Ethnobiol. and Ethnomed. 2018, 14, 70. [Google Scholar] [CrossRef] [PubMed]
  18. Department of Social Development and Welfare. Highland Communities Within 20 Provinces of Thailand; Ministry of Social Development and Human Security: Bangkok, Thailand, 2016.
  19. Young, G. The Hill Tribes in Northern Thailand; Siam Society: Bangkok, Thailand, 1962. [Google Scholar]
  20. Schmidt-Vogt, D. Secondary forests in swidden agriculture in the highlands of Thailand. J. Trop. For. Sci. 2001, 13, 748–767. [Google Scholar]
  21. Schmidt-Vogt, D. Defining Degradation: The impacts of swidden on forests in Northern Thailand. Mt. Res. Dev. 1998, 18, 135–149. [Google Scholar] [CrossRef]
  22. Inta, A.; Shengji, P.; Balslev, H.; Wangpakapattanawong, P.; Trisonthi, C. A comparative study on medicinal plants used in Akha’s traditional medicine in China and Thailand, cultural coherence or ecological divergence? J. Ethnopharmacol. 2008, 116, 508–517. [Google Scholar] [CrossRef]
  23. Inta, A.; Trisonthi, P.; Trisonthi, C. Analysis of traditional knowledge in medicinal plants used by Yuan in Thailand. J. Ethnopharmacol. 2013, 149, 344–351. [Google Scholar] [CrossRef]
  24. Junsongduang, A.; Balslev, H.; Inta, A.; Jampeetong, A.; Wangpakapattanawong, P. Medicinal plants from swidden fallows and sacred forest of the Karen and the Lawa in Thailand. J. Ethnobiol. Ethnomedicine 2013, 9, 44. [Google Scholar] [CrossRef] [Green Version]
  25. Junsongduang, A.; Balslev, H.; Jampeetong, A.; Inta, A.; Wangpakapattanawong, P. Woody plant diversity in sacred forests and fallows in Chiang Mai, Thailand. Chiang Mai J. Sci. 2014, 41, 1132–1149. [Google Scholar]
  26. Khuankaew, S.; Srithi, K.; Tiansawat, P.; Jampeetong, A.; Inta, A.; Wangpakapattanawong, P. Ethnobotanical study of medicinal plants used by Tai Yai in Northern Thailand. J. Ethnopharmacol. 2014, 151, 829–838. [Google Scholar] [CrossRef]
  27. Panyadee, P.; Balslev, H.; Wangpakapattanawong, P.; Inta, A. Woody plant diversity in urban homegardens in Northern Thailand. Econ. Bot. 2016, 70, 285–302. [Google Scholar] [CrossRef]
  28. Phumthum, M.; Srithi, K.; Inta, A.; Junsongduang, A.; Tangjitman, K.; Pongamornkul, W.; Trisonthi, C.; Balslev, H. Ethnomedicinal plant diversity in Thailand. J. Ethnopharmacol. 2018, 214, 90–98. [Google Scholar] [CrossRef] [PubMed]
  29. Punchay, K.; Inta, A.; Tiansawat, P.; Balslev, H.; Wangpakapattanawong, P. Traditional knowledge of wild food plants of Thai Karen and Lawa (Thailand). Genet. Res. Crop. Evol. 2020, 67, 1277–1299. [Google Scholar] [CrossRef]
  30. Kantasrila, R.; Pandith, H.; Balslev, H.; Wangpakapattanawong, P.; Panyadee, P.; Inta, A. Medicinal plants for treating musculoskeletal disorders among Karen in Thailand. Plants 2020, 9, 811. [Google Scholar] [CrossRef] [PubMed]
  31. Srithi, K.; Balslev, H.; Wangpakapattanawong, P.; Srisanga, P.; Trisonthi, C. Medicinal plant knowledge and its erosion among the Mien (Yao) in northern Thailand. J. Ethnopharmacol. 2009, 123, 335–342. [Google Scholar] [CrossRef]
  32. Srithi, K.; Trisonthi, C.; Wangpakapattanawong, P.; Balslev, H. Medicinal plants used in Hmong women’s healthcare in northern Thailand. J. Ethnopharmacol. 2012, 139, 119–135. [Google Scholar] [CrossRef]
  33. Srithi, K.; Trisonthi, C.; Wangpakapattanawong, P.; Srisanga, P.; Balslev, H. Plant diversity in Hmong and Mien homegardens in northern Thailand. Econ. Bot. 2012, 66, 192–206. [Google Scholar] [CrossRef]
  34. Tangjitman, K.; Wongsawad, C.; Kamwong, K.; Sukkho, T.; Trisonthi, C. Ethnomedicinal plants used for digestive system disorders by the Karen of northern Thailand. J. Ethnobiol. Ethnomed. 2015, 11, 27. [Google Scholar] [CrossRef] [Green Version]
  35. Tangjitman, K.; Wongsawad, C.; Winijchaiyanan, P.; Sukkho, T.; Kamwong, K.; Pongamornkul, W.; Trisonthi, C. Traditional knowledge on medicinal plant of the Karen in northern Thailand: A comparative study. J. Ethnopharmacol. 2013, 150, 232–243. [Google Scholar] [CrossRef]
  36. Trisonthi, C.; Trisonthi, P. Ethnobotanical study in Thailand: A case study in Khun Yuam district, Mae Hong Son province. Thai J. Bot. 2009, 1, 1–23. [Google Scholar]
  37. Trisonthi, C.; Trisonthi, P. Ethnobotany of Lua and H’tin on Doi Phukha, Nan Province. Thai J. Bot. 2011, 3, 163–185. [Google Scholar]
  38. Turreira-García, N.; Vilkamaa, A.M.; Byg, A.; Theilade, I. Diversity, knowledge, and use of leafy vegetables in northern Thailand—Maintenance and transmission of ethnobotanical knowledge during urbanisation. Nat. Hist. Bull. Siam Soc. 2017, 62, 85–105. [Google Scholar]
  39. Pongamornkul, W.; Trisonthi, C.; Trisonthi, P.; Inta, A. Northern Thailand Ethnobotanical Index; The Botanical Garden Organization, Ministry of Natural Resource and Environment: Chiang Mai, Thailand, 2017. [Google Scholar]
  40. Tienboon, P. Macronutrient status of Karen hill tribe children aged 1–6 years in Northern Thailand. Thai J. Clin. Nutr. 2010, 4, 83–87. [Google Scholar]
  41. Tienboon, P.; Wangpakapattanawong, P. Nutritional status, body composition and health conditions of the Karen hill tribe children aged 1–6 years in Northern Thailand. Asia Pac. J. Clin. Nutr. 2007, 16, 279–285. [Google Scholar] [PubMed]
  42. Tienboon, P.; Wangpakapattanawong, P. Vitamin A status of the minority ethnic group of Karen hill tribe children aged 1–6 years in Northern Thailand. Asia Pac. J. Clin. Nutr. 2007, 16, 158–162. [Google Scholar] [PubMed]
  43. Tienboon, P.; Wangpakapattanawong, P.; Thomas, D.E.; Kimmins, J.P. Vitamins and minerals status of Karen hill tribe children aged 1–6 years in Northern Thailand. Thai J. Clin.Nutr. 2008, 2, 34–38. [Google Scholar]
  44. Phillips, K.M.; Pehrsson, P.R.; Agnew, W.W.; Scheett, A.J.; Follett, J.R.; Lukaski, H.C.; Patterson, K.Y. Nutrient composition of selected traditional United States Northern Plains Native American plant foods. J. Food Compos. Anal. 2014, 34, 136–152. [Google Scholar] [CrossRef] [Green Version]
  45. Sotelo, A.; López-García, S.; Basurto-Peña, F. Content of nutrient and antinutrient in edible flowers of wild plants in Mexico. Plant. Food Hum. Nutr. 2007, 62, 133–138. [Google Scholar] [CrossRef]
  46. Pawera, L.; Khomsan, A.; Zuhud, E.A.M.; Hunter, D.; Ickowitz, A.; Polesny, Z. Wild food plants and trends in their use: From knowledge and perceptions to drivers of change in West Sumatra, Indonesia. Foods 2020, 9, 1240. [Google Scholar] [CrossRef]
  47. FAO; IFAD; UNICEF; WFP; WHO. The State of Food Security and Nutrition in the World 2020 Transforming Food Systems for Affordable Healthy Diets; Food and Agriculture Organization of the United Nations: Rome, Italy, 2020.
  48. Wessells, K.R.; Brown, K.H. Estimating the global prevalence of zinc deficiency: Results based on zinc availability in national food supplies and the prevalence of stunting. PLoS ONE 2012, 7, e50568. [Google Scholar] [CrossRef] [Green Version]
  49. Rojroongwasinkul, N.; Kijboonchoo, K.; Wimonpeerapattana, W.; Purttiponthanee, S.; Yamborisut, U.; Boonpraderm, A.; Kunapan, P.; Thasanasuwan, W.; Khouw, I. SEANUTS: The nutritional status and dietary intakes of 0.5–12-year-old Thai children. Brit. J. Nutr. 2013, 110, S36–S44. [Google Scholar] [CrossRef] [Green Version]
  50. Roesler, A.L.; Smithers, L.G.; Wangpakapattanawong, P.; Moore, V. Stunting, dietary diversity and household food insecurity among children under 5 years in ethnic communities of Northern Thailand. J. Public Health 2018, 41, 772–780. [Google Scholar] [CrossRef] [PubMed]
  51. Sang-ngoen, D.; Hutchinson, C.; Satheannoppakao, W.; Tipayamongkholgul, M. Dietary iron intake and availability in hill tribe and urban women, Chiang Rai province, Northern Thailand. Ecol. Food Nutr. 2020, 59, 399–419. [Google Scholar] [CrossRef] [PubMed]
  52. Pieroni, A. Evaluation of the cultural significance of wild food botanicals traditionally consumed in Northwestern Tuscany, Italy. J. Ethnobiol. 2001, 21, 89–104. [Google Scholar]
  53. Sujarwo, W.; Caneva, G. Using quantitative indices to evaluate the cultural importance of food and nutraceutical plants: Comparative data from the Island of Bali (Indonesia). J. Cult. Herit. 2016, 18, 342–348. [Google Scholar] [CrossRef]
  54. International Society of Ethnobiology. International Society of Ethnobiology Code of Ethics (with 2008 additions). Available online: http://ethnobiology.net/code-of-ethics/ (accessed on 14 November 2020).
  55. World Flora Online. Available online: http://www.worldfloraonline.org (accessed on 3 August 2020).
  56. Horwitz, W.; Latimer, G.W. Official Methods of Aanalysis of AOAC International, 18th ed.; Association of Official Agricultural Chemists International: Gaithersburg, MD, USA, 2005. [Google Scholar]
  57. Kalra, Y. Handbook of Reference Methods for Plant. Analysis; CRC Press: Boca Raton, FL, USA, 1997. [Google Scholar]
  58. Alam, M.K.; Rana, Z.H.; Islam, S.N. Comparison of the proximate composition, total carotenoids and total polyphenol content of nine orange-fleshed sweet potato varieties grown in Bangladesh. Foods 2016, 5, 64. [Google Scholar] [CrossRef] [Green Version]
  59. Medicine, I.; Meyers, L.D.; Hellwig, J.P.; Otten, J.J. Dietary Reference Intakes: The Essential Guide to Nutrient Requirements; National Academies Press: Washington, DC, USA, 2006. [Google Scholar]
  60. Committees of Dietary Reference Intake for Thais. Dietary Reference Intake for Thais 2020; Bureau of Nutrition, Department of Health, Ministry of Public Health: Bangkok, Thailand, 2020.
  61. Garibay-Orijel, R.; Caballero, J.; Estrada-Torres, A.; Cifuentes, J. Understanding cultural significance, the edible mushrooms case. J. Ethnobiol. Ethnomed. 2007, 3, 4. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  62. Alonso-Aguilar, L.E.; Montoya, A.; Kong, A.; Estrada-Torres, A.; Garibay-Orijel, R. The cultural significance of wild mushrooms in San Mateo Huexoyucan, Tlaxcala, Mexico. J. Ethnobiol. Ethnomed. 2014, 10, 27. [Google Scholar] [CrossRef] [Green Version]
  63. Thakur, D.; Sharma, A.; Uniyal, S.K. Why they eat, what they eat: Patterns of wild edible plants consumption in a tribal area of western Himalaya. J. Ethnobiol. Ethnomed. 2017, 13, 70. [Google Scholar] [CrossRef] [Green Version]
  64. Sõukand, R. Perceived reasons for changes in the use of wild food plants in Saaremaa, Estonia. Appetite 2016, 107, 231–241. [Google Scholar] [CrossRef]
  65. Schönfeldt, H.C.; Pretorius, B. The nutrient content of five traditional South African dark green leafy vegetables—A preliminary study. J. Food Compos. Anal. 2011, 24, 1141–1146. [Google Scholar] [CrossRef]
  66. Patricia, O.; Zoue, L.; Mégnanou, R.-M.; Doue, R.; Niamke, S. Proximate composition and nutritive value of leafy vegetables consumed in Northern Cote d’Ivoire. Eur. Sci. J. 2014, 10, 212–227. [Google Scholar]
  67. Rachkeeree, A.; Kantadoung, K.; Suksathan, R.; Puangpradab, R.; Page, P.A.; Sommano, S.R. Nutritional compositions and phytochemical properties of the edible flowers from selected Zingiberaceae found in Thailand. Front. Nutr. 2018, 5, 3. [Google Scholar] [CrossRef] [Green Version]
  68. Gupta, S.; Jyothi Lakshmi, A.; Manjunath, M.N.; Prakash, J. Analysis of nutrient and antinutrient content of underutilized green leafy vegetables. LWT-Food Sci. Technol 2005, 38, 339–345. [Google Scholar] [CrossRef]
  69. Kwenin, W.; Wolli, M.; Dzomeku, B.J.J.o.A.; Sciences, P. Assessing the nutritional value of some African indigenous green leafy vegetables in Ghana. J. Anim. Plant. Sci. 2011, 10, 1300–1305. [Google Scholar]
  70. Abbasi, A.M.; Shah, M.H.; Khan, M.A. Wild Edible Vegetables of Lesser Himalayas: Ethnobotanical and Nutraceutical Aspects; Springer International Publishing: Cham, Switzerland, 2014. [Google Scholar]
  71. Aberoumand, A. Preliminary assessment of nutritional value of plant-based diets in relation to human nutrients. Int. J. Food Sci. Nutr. 2009, 60, 155–162. [Google Scholar] [CrossRef] [PubMed]
  72. Datta, S.; Sinha, B.K.; Bhattacharjee, S.; Seal, T. Nutritional composition, mineral content, antioxidant activity and quantitative estimation of water soluble vitamins and phenolics by RP-HPLC in some lesser used wild edible plants. Heliyon 2019, 5, e01431. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  73. US Department of Agriculture, Agricultural Research Service. USDA National Nutrient Database for Standard Reference, Release 28 (Slightly Revised). Nutrient Data Laboratory. Available online: http://www.ars.usda.gov/nea/bhnrc/mafcl (accessed on 25 November 2020).
  74. EFSA Panel on Dietetic Products Nutrition, and Allergies. Scientific Opinion on Dietary Reference Values for carbohydrates and dietary fibre. EFSA J. 2010, 8, 1462. [Google Scholar]
  75. Slavin, J. Fiber and prebiotics: Mechanisms and health benefits. Nutrients 2013, 5, 1417–1435. [Google Scholar] [CrossRef] [Green Version]
  76. Ekwumemgbo, P.A.; Sallau, M.S.; Omoniyi, K.I.; Zubairu, S.Y. Proximate and anti-nutritional constituents of Abelmoschus esculentus grown in Fadaman Kubanni, Zaria, Kaduna State. Niger. J. Sci. Res. Rep. 2014, 3, 2015–2027. [Google Scholar]
  77. Sarker, U.; Oba, S. Nutrients, minerals, pigments, phytochemicals, and radical scavenging activity in Amaranthus blitum leafy vegetables. Sci. Rep.-UK 2020, 10, 3868. [Google Scholar] [CrossRef] [Green Version]
  78. Puwastien, P.; Burlingame, B.; Raroengwichit, M.; Sungpuag, P. ASEAN Food Composition Tables. Available online: http://www.inmu.mahidol.ac.th/aseanfoods/doc/OnlineASEAN_FCD_V1_2014.pdf (accessed on 22 September 2020).
  79. Sritalahareuthai, V.; Aursalung, A.; On-nom, N.; Temviriyanukul, P.; Charoenkiatkul, S.; Suttisansanee, U. Nutritional composition of conserved Kadsura spp. plants in Northern Thailand. Heliyon 2020, 6, e04451. [Google Scholar] [CrossRef] [PubMed]
  80. Rana, Z.H.; Alam, M.K.; Akhtaruzzaman, M. Nutritional composition, total phenolic content, antioxidant and α-amylase inhibitory activities of different fractions of selected wild edible plants. Antioxidants 2019, 8, 203. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  81. Agency for Toxic Substances and Disease Registry. Toxicological Profile for Manganese; United States Department of Health and Human Services: Washington, DC, USA, 2012.
  82. Buchman, A.L. Manganese. In Modern nutrition in health and disease; Ross, C.A., Caballero, B., Cousins, R.J., Tucker, K.L., Ziegler, T.R., Eds.; Lippincott Williams & Wilkins: Philadelphia, PA, USA, 2014; pp. 238–244. [Google Scholar]
  83. Pintawong., C.; Nontaso, A.; Kawinate, S. Guidelines for Management of Manganese Mineral Resources. Available online: http://www.dmr.go.th/download/law_minerals/Manganese.pdf (accessed on 3 October 2020).
Figure 1. The relationship between twelve leafy vegetable species and the elements of CFSI in two Karen and two Lawa villages in northern Thailand. (AI = availability index; FUI = frequency of utilization index; PUI = plant parts used index; MFFI = multi-functional food use index; TSAI = taste score appreciation index; and FMRI = food-medicinal role index). The thicker the band, the more informants mentioned the relationship.
Figure 1. The relationship between twelve leafy vegetable species and the elements of CFSI in two Karen and two Lawa villages in northern Thailand. (AI = availability index; FUI = frequency of utilization index; PUI = plant parts used index; MFFI = multi-functional food use index; TSAI = taste score appreciation index; and FMRI = food-medicinal role index). The thicker the band, the more informants mentioned the relationship.
Foods 09 01748 g001
Table 1. Twelve wild leafy vegetable species encountered in two Karen and two Lawa villages in northern Thailand, giving their scientific name, family, common name in English, ethnobotanical information, distribution, collection period, and their Cultural Food Significance Index (CFSI) values.
Table 1. Twelve wild leafy vegetable species encountered in two Karen and two Lawa villages in northern Thailand, giving their scientific name, family, common name in English, ethnobotanical information, distribution, collection period, and their Cultural Food Significance Index (CFSI) values.
Scientific Name (Family); Voucher Number (Punchay # Deposited at CMUB)Folk Name [29]Traditional Use by the Karen (K) and the Lawa (L) [29]DistributionCollection PeriodCFSI Score
Oroxylum indicum (L.) Kurz (Bignoniaceae) 566Do ka (K)
Dak ra wi (L)
Young shoots or fruits eaten raw or cooked. Inner bark grated and added to food for bitter taste (K, L).AsiaAll year813
Centella asiatica (L.) Urb. (Apiaceae) 546Sui po na do (K)
Phak nhok (L)
Aerial parts eaten raw as a side dish for treating bruises (K, L). Africa, Asia, North- and South America, and OceaniaAll year629
Senegalia rugata (Lam.) Britton and Rose (Leguminosae) 605Pa chi (K)
Kad ka ha (L)
Young shoots eaten raw or cooked with fish (K, L).Asia and OceaniaAll year437
Ficus auriculata Lour. (Moraceae) 542Ta kue po (K)
Mae (L)
Shoots boiled as a side dish or cooked (K, L).AsiaMay–Oct432
Clerodendrum glandulosum Lindl. (Lamiaceae) 304Ko ko do (K)
Tung lam (L)
Young leaves boiled and pressed to reduce bitter taste, then fried with eggs or cooked as soup (K, L).AsiaDec–Apr392
Spondias pinnata (L. f.) Kurz (Anacardiaceae) 443Pi sae (K)
Kok (L)
Young leaves eaten raw as a side dish (K, L). Stems decocted for treating diarrhea (K).AsiaJun–Jan379
Lygodium flexuosum (L.) Sw. (Lygodiaceae) 457Ki ko do (K)
Wu wia (L)
Shoots boiled as a side dish or cooked (K, L). Roots boiled as a beverage (tea) (K).Asia and OceaniaMay–Feb378
Oenanthe javanica (Blume) DC. (Apiaceae) 564Po a do (K)
Tu klae (L)
Aerial parts eaten raw as a side dish (K, L).AsiaJun–Dec365
Acmella paniculata (Wall. ex DC.) R.K.Jansen (Asteraceae) 594Hor te mi (K)
Tu plei (L)
Aerial parts eaten raw with chili paste or cooked (K, L). Roots chewed to treat toothache (K).AsiaJun–Jan353
Acmella uliginosa (Sw.) Cass. (Asteraceae) 522Hor te mi (K)
Tu plei (L)
Aerial parts eaten raw with chili paste or cooked. Roots chewed to treat toothache (K, L).Native pantropicalJun–Jan353
Monochoria vaginalis (Burm.f.) C.Presl (Pontederiaceae) 690No do (K)
Seuk lek (L)
Young shoots and petioles eaten raw or cooked (K, L).Asia and North America (introduced)May–Sep336
Musa acuminata Colla (Musaceae) 536Ya pa la (K)
Lha wong pia (L)
Pseudostems chopped and cooked as soup/or used as fodder; inflorescences were eaten raw or cooked (K, L). Throughout tropics in Africa, America, and AsiaAll year308
Table 2. Proximate composition of the edible parts of selected wild food plant species (g/100 g fresh weight).
Table 2. Proximate composition of the edible parts of selected wild food plant species (g/100 g fresh weight).
SpeciesMoisture ContentAshProtein Fat Fiber Carbohydrate
Acmella paniculata87.4 ± 1.6 c1.7 ± 0.2 bc2.92 ± 0.4 de0.55 ± 0.07 f2.17 ± 0.2 bc5.24 ± 0.8 c
Acmella uliginosa88.9 ± 1.5 c1.4 ± 0.2 abc3.58 ± 0.1 e0.34 ± 0.03 cd1.46 ± 0.3 ab4.17 ± 0.6 bc
Centella asiatica87.6 ± 1.7 c1.8 ± 0.2 bc2.71 ± 0.4 a0.32 ± 0.04 cd1.84 ± 0.3 abc5.69 ± 0.8 c
Clerodendum glandulosum76.3 ± 1.8 b1.8 ± 0.1 bc5.33 ± 0.4 f0.48 ± 0.04 ef3.01 ± 0.3 cd13.08 ± 1.0 e
Ficus auriculata86.6 ± 1.1 c1.9 ± 0.1 c2.89 ± 0.3 de0.34 ± 0.03 cd3.77 ± 0.3 e4.47 ± 0.4 bc
Lygodium flexuosum62.9 ± 2.6 a2.8 ± 0.2 d3.78 ± 0.3 e0.78 ± 0.07 g11.82 ± 0.7 e17.94 ± 1.3 f
Monochoria vaginalis94.8 ± 1.2 d1.1 ± 0.2 ab0.56 ± 0.1 ab0.11 ± 0.03 a0.79 ± 0.2 a2.63 ± 0.6 ab
Musa acuminata95.3 ± 1.0 d1.2 ± 0.2 ab0.48 ± 0.1 a0.10 ± 0.02 a1.36 ± 0.3 ab1.54 ± 0.4 a
Oenanthe javanica88.7 ± 3.0 c2.1 ± 0.5 cd1.85 ± 0.4 cd0.17 ± 0.05 ab2.87 ± 0.7 cd4.26 ± 1.3 bc
Oroxylum indicum86.8 ± 1.0 c0.8 ± 0.1 a1.46 ± 0.1 bc0.26 ± 0.02 bc2.03 ± 0.2 bc8.65 ± 0.7 d
Senegalia rugata85.7 ± 1.7 c0.8 ± 0.1 a4.77 ± 0.6 f0.41 ± 0.05 de3.98 ± 0.5 e4.32 ± 0.5 bc
Spondias pinnata75.6 ± 0.8 b4.0 ± 0.3 e3.61 ± 0.1 e0.74 ± 0.03 g3.84 ± 0.4 e11.93 ± 0.4 e
a–e In each column, different letters at the end of each value represent the differences of the mineral content among plant species (Tukey’s HSD test). The species sharing the same letter were not significantly different in their mineral contents.
Table 3. Mineral composition (mg/100 g fresh weight) in twelve wild food plant species sampled in two Karen and two Lawa villages in northern Thailand. The figures are compared to the recommended dietary allowance (RDA) and tolerable upper intake level (UL) according to [59].
Table 3. Mineral composition (mg/100 g fresh weight) in twelve wild food plant species sampled in two Karen and two Lawa villages in northern Thailand. The figures are compared to the recommended dietary allowance (RDA) and tolerable upper intake level (UL) according to [59].
SpeciesPlant partPKCaMgNaFeMnZnCu
Acmella paniculataAerial parts40.5 ± 0.5 de356.2 ± 1.1 ab183.4 ± 4.5 c55.3 ± 2.0 ef1.8 ± 0.1 abc11.1 ± 1.2 e1.8 ± 1.1 ab6.7 ± 1.10 de0.04 ± 0.00 d
Acmella uliginosaAerial parts44.2 ± 0.6 f549.7 ± 9.9 cde147.8 ± 1.8 b56.5 ± 1.1 f0.7 ± 0.1 a10.7 ± 0.3 e7.1 ± 1.0 c1.9 ± 0.19 ab0.09 ± 0.00 f
Centella asiaticaLeaves32.2 ± 1.4 c377.0 ± 42.0 abc176.7 ± 10.5 bc104.4 ± 2.8 h21.2 ± 1.6 e4.1 ± 0.2 bc12.0 ± 0.7 de10.9 ± 1.86 f0.02 ± 0.00 b
Clerodendum glandulosumYoung leaves71.1 ± 2.9 h693.7 ± 11.9 e24.7 ± 3.1 a69.8 ± 3.2 g1.5 ± 0.1 abc2.2 ± 0.1 ab10.9 ± 1.5 d19.4 ± 2.63 h0.34 ± 0.01 g
Ficus auriculataYoung leaves48.6 ± 1.1 g447.2 ± 7.7 bcd338.1 ± 15.2 d50.1 ± 3.2 de4.8 ± 1.1 d5.5 ± 0.1 bc3.3 ± 0.3 b5.7 ± 0.34 cd0.05 ± 0.00 e
Lygodium flexuosumYoung leaves44.2 ± 1.9 f668.3 ± 21.8 e15.4 ± 0.8 a57.4 ± 3.6 f2.4 ± 0.4 c6.3 ± 4.3 cd14.0 ± 1.3 ef7.0 ± 0.68 de0.03 ± 0.00 cd
Monochoria vaginalisLeaves16.4 ± 0.4 b253.4 ± 10.9 a28.5 ± 1.6 a12.4 ± 0.6 bc0.8 ± 0.1 ab9.3 ± 0.2 de15.7 ± 0.3 f3.0 ± 0.42 abc<0.01 a
Musa acuminataPsuedostem9.3 ± 1.0 a591.0 ± 25.5 de2.6 ± 0.1 a8.0 ± 0.8 ab0.4 ± 0.1 a0.4 ± 0.1 a6.3 ± 0.9 c4.6 ± 0.5 bcd<0.01 a
Oenanthe javanicaAerial parts43.5 ± 1.5 ef1291.3 ± 254 f170.2 ± 12.0 bc46.4 ± 0.8 d2.2 ± 0.1 bc7.0 ± 0.6 cd8.4 ± 0.5 c14.0 ± 0.5 g0.06 ± 0.00 e
Oroxylum indicumFruits31.0 ± 1.0 c235.3 ± 9.2 a3.0 ± 0.4 a14.2 ± 2.1 c0.5 ± 0.0 a0.3 ± 0.0 a0.2 ± 0.0 a6.4 ± 0.9 de0.41 ± 0.01 h
Senegalia rugataYoung leaves77.7 ± 1.5 i221.7 ± 11.2 a1.0 ± 0.1 a13.4 ± 1.0 bc0.9 ± 0.1 ab0.7 ± 0.0 a0.4 ± 0.0 a9.0 ± 1.1 ef0.01 ± 0.00 ab
Spondias pinnataYoung leaves37.8 ± 1.4 d244.8 ± 35.5 a982.9 ± 37.2 e6.0 ± 0.2 a1.2 ± 0.4 abc2.4 ± 0.4 ab8.1 ± 1.1 c1.4 ± 0.2 a0.02 ± 0.00 bc
RDA 1 and UL 2
Male700‒(4000)4700 *1000‒(2500)330‒(350) **1500‒(2300)8‒(45)2.3‒(11)11‒(40)0.9‒(10)
Female700‒(4000)4700 *1000‒(2500)255‒(350) **1500‒(2300)18‒(45)1.8‒(11)8‒(40)0.9‒(10)
Pregnancy700‒(3500)4700 *1000‒(2500)290‒(350) **1500‒(2300)27‒(45)2.0‒(11)11‒(40)1‒(8)
Lactation700‒(4000)5100 *1000‒(2500)255‒(350) **1500‒(2300)9‒(45)2.6‒(11)12‒(40)1.3‒(8)
a–i In each column, different letters at the end of each value represent the differences in the mineral content among plant species (Tukey’s HSD test). The species sharing the same letter were not significantly different in their mineral contents. 1 Recommended dietary allowance in adults aged 19‒50 years (mg/day); 2 Tolerable upper intake level in adults aged 19‒50 years (mg/day) [59]. * For the absence of a UL, extra caution may be warranted in consuming levels above the recommended intake. ** The UL for magnesium represents intake from pharmacological agents only and does not include intake from food and water.
Table 4. Percentages of contribution to the recommended dietary allowance (RDA) (mg/day) [59], for adults, of macrominerals (P, K, Ca, Mg, and Na) and trace minerals (Fe, Mn, Zn, and Cu).
Table 4. Percentages of contribution to the recommended dietary allowance (RDA) (mg/day) [59], for adults, of macrominerals (P, K, Ca, Mg, and Na) and trace minerals (Fe, Mn, Zn, and Cu).
Scientific Name% of RDA (Male/Female)
PKCaMgNa
Acmella paniculata571816/210.12
Acmella uliginosa6111417/220.04
Centella asiatica481731/411.41
Clerodendum glandulosum1014221/270.10
Ficus auriculata793315/190.32
Lygodium flexuosum614117/220.16
Monochoria vaginalis2523/40.05
Musa acuminata1120.22/30.02
Oenanthe javanica6271714/180.14
Oroxylum indicum450.34/50.03
Senegalia rugata1140.14/50.06
Spondias pinnata55981/20.08
Scientific Name % of RDA (Male/Female)
FeMnZnCu
Acmella paniculata 138/6178/10060/834
Acmella uliginosa 133/59308/39417/2310
Centella asiatica 51/22521/66699/1362.2
Clerodendum glandulosum 27/12389/605176/24237
Ficus auriculata 68/30143/18351/715
Lygodium flexuosum 78/35608/77763/873
Monochoria vaginalis 116/51682/87227/37<1
Musa acuminata 5/2273/35041/57<1
Oenanthe javanica 87/38365/466127/1756
Oroxylum indicum 3/18/1158/8045
Senegalia rugata 8./317/2281/1121
Spondias pinnata 30/13352/45012/172
The percentages of RDA values for macrominerals and trace minerals are compared with the consumptions of 100 g of fresh leafy vegetables. The percentages of RDA values of P, K, Ca, Na, and Cu, in male and female adults (19–50 years) are equal.
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Punchay, K.; Inta, A.; Tiansawat, P.; Balslev, H.; Wangpakapattanawong, P. Nutrient and Mineral Compositions of Wild Leafy Vegetables of the Karen and Lawa Communities in Thailand. Foods 2020, 9, 1748. https://doi.org/10.3390/foods9121748

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Punchay K, Inta A, Tiansawat P, Balslev H, Wangpakapattanawong P. Nutrient and Mineral Compositions of Wild Leafy Vegetables of the Karen and Lawa Communities in Thailand. Foods. 2020; 9(12):1748. https://doi.org/10.3390/foods9121748

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Punchay, Kittiyut, Angkhana Inta, Pimonrat Tiansawat, Henrik Balslev, and Prasit Wangpakapattanawong. 2020. "Nutrient and Mineral Compositions of Wild Leafy Vegetables of the Karen and Lawa Communities in Thailand" Foods 9, no. 12: 1748. https://doi.org/10.3390/foods9121748

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Punchay, K., Inta, A., Tiansawat, P., Balslev, H., & Wangpakapattanawong, P. (2020). Nutrient and Mineral Compositions of Wild Leafy Vegetables of the Karen and Lawa Communities in Thailand. Foods, 9(12), 1748. https://doi.org/10.3390/foods9121748

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