Skip to main content

Nutritional potential of underutilized edible plant species in coffee agroforestry systems of Yayu, southwestern Ethiopia

Abstract

Ethiopia is confronted with the paradox of hosting hundreds of edible plants and having high food and nutritional insecurity. Meals are mainly made up of staples and often lack of protein and micronutrients. Therefore, a large section of the population, particularly children and women, are malnourished. We hypothesize that wild edible plant species can contribute to fulfil the micronutrient demands of local people. Hence, we assessed the nutritional potential of underutilized edible plant species growing in understories of coffee agroforestry systems of southwestern Ethiopia. An ethnobotanical household survey (n = 300) documented the edible existing plants; and a promising subset of them (n = 12) was analysed for nutrient and antinutritional factor content in the lab. All 12 species, except fruits, have higher calcium, iron and zinc contents compared to regularly cultivated crops. Vitamin C was high in Syzygium guineense (330.72 mg/100 g edible parts or EP) and Rubus apetalus (294.19 mg/100 g). Beta-carotene ranged from 9.2 to 75 µg retinol activity equivalent (RAE) /100 g 25 among all species, but was exceptionally high in Rubus apetalus (161.7 µg RAE/100 g). Concerning the antinutritional factors, phytate content varied from 31.06 to 601.65 µg/100 g, being lower in Dioscorea prehensilis (31.06 µg/100 g) and D. alata (90.17 µg/100 g) compared to Carissa spinarum (601.65 µg/100 g) and Solanum nigrum (536.48 µg/100 g). Thus, we conclude that the assessed underutilized species are potential sources of dietary nutrients locally needed, and are notable Amaranthus graecizans, Portulaca oleracea and Dioscorea cayenensis as providers of Ca, Fe and Zn, and the fruit Rubus apetalus of provitamin A.

Introduction

The global food system depends on only a few species. Nowadays, about 70–90% of all vegetable calories consumed by humans are derived from rice, wheat, maize, sugar, sorghum, millet and cassava (Pimentel et al. 2007), while in the past about 7000 plant species were regularly cultivated, mostly for food (Frison and Padulosi 1999). The main reason for the decline is the rise of modern agriculture (Khoury et al. 2014), which has affected the cultivation of indigenous vegetables, fruits, and other food plants (Khoury et al. 2014). This process is continuing, as there is little attention to local, traditional, and (semi)wild species (Grivetti and Ogle 2000).

In Africa, several species of high nutritional value are customarily cultivated or consumed. E.g., Adansonia digitata, Balanites aegyptiaca, Ziziphus mauritiana, Boscia senegalensis and Cassia obtusifolia, are key suppliers of the pro-vitamins A, B2 and C (Becker 1983), Amaranthus viridis and Hibiscus sabdariffa are important providers of protein, fatty acids, iron (Fe), magnesium (Mg), calcium (Ca) and zinc (Zn) (Sena et al. 1998). In Ethiopia, the nutritional importance of safflower (Carthamus tinctorius), tef (Eragrostis tef), noug (Guizotia abyssinica), and enset (Ensete ventricosum) is broadly acknowledged. Nevertheless, 38% of the Ethiopian children under 5 years suffer from chronic malnutrition (stunting or low weight-for-age), and 22% of the women of the reproductive age are undernourished, and therefore predisposed to have children of low birth weight and height, and of having high risk of disease and even death, situation that is exacerbated in rural areas (CSA and ICF 2016).

This critical situation of rural Ethiopia is due to several reasons, e.g., limited food availability and accessibility, inappropriate child feeding practices, deficient norms regarding food safety, limited access to health care, etc. (Beyero et al. 2015), but the unbalanced diet seems to be among the most important. Although staple crops such as tef (Eragrostis tef), enset (Ensete ventricosum), maize (Zea mays), wheat (Triticum aestivum), yam (Dioscorea spp.), etc. are widely cultivated and consumed (Fentahun and Hager 2009), the consumption of vegetables and fruits is limited. Even when farmers grow these, they are sold to supplement the household income and not for self-consumption. Consequently, diets are often deficient in protein and micronutrients, such as Fe, Ca and vitamin A (Sheehy et al. 2019; Baye et al. 2019). In rural Ethiopia the risk of vitamin A deficiency reaches 60.3% and of iron 86.3% (Seyoum et al. 2018).

The evidence suggests that nutrition-sensitive agriculture interventions can have a positive impact on dietary diversity (FAO 2017), and that growing various foods diversify the diets and improves the nutritional status of individuals. In this regard, an important alternative are the underutilized, semi-domesticated, wild crop species. Underutilized plant species are those whose cultivation has been neglected due to various constraints, e.g. require traditional management, are suited to specific environments, need laborious processing, are subject of poor grading and packaging, their taste is unfamiliar, their nutritional properties are unknown, and even are subjects of social taboos (Padulosi et al. 2013; Cernansky 2015). Underutilized species have long been part of local cultures and traditions in many parts of the world. For instance, about 300 million people collect products from the forests (Bharuch and Pretty 2010) that regularly include fruits, leafy vegetables, nuts, seeds and edible oils (Belcher et al. 2005). These species support diet diversification and address seasonal food and nutritional gaps by what is called “hidden harvest” (Pol 2002, Power et al. 2015). Furthermore, they are bonded to the land uses different to agriculture (e.g. forests), and come under pressure as their habitats deteriorate through agricultural expansion (Senbeta et al. 2010). Thus, many of these underutilized species, along with the traditional knowledge about their cultivation and use, are being lost at an alarming rate. Moreover, despite their value and contribution to the global food basket, underutilized species are often excluded from official statistics in terms of their economic value (Bharuch and Pretty 2010).

In Ethiopia, over 200 wild and semi-domesticated edible plant species have been documented (Fentahun and Hager 2009; Senbeta et al. 2010; Lulekal et al. 2011). Notable is the prevailing negative connotation bonded to their use (Fentahun and Hager 2009), which is related to the homogenization of eating habits that exclude them, the lack of information about their nutritional value, and the limited knowledge on their production and postproduction (Balemie and Kebebew 2006). The underutilization and marginalization of these species may also be attributed to the lack of scientific knowledge on their nutritional and antinutritional properties, which is the raison d'être of this study: to identify, characterize and determine the nutritional content of selected underutilized edible plants in agroforestry systems of southwestern Ethiopia.

Materials and methods

This study combined various methods, which included households surveying, experts interviews, botanical characterization and biochemical laboratory analyses, which were ensembled to provide a comprehensive view on the local underutilized species.

Study site

This study was undertaken in the Yayu area of southwestern Ethiopia, from May to December 2016. The area comprised of six Woredas (districts), out of which four, namely Chora, Doreni, Hurumu and Yayu, were selected for sampling. The Yayu area is regarded as having the highest forest cover in Ethiopia (Tulu 2010). It is characterized by a rolling topography, dissected by two major rivers: Geba and Dogi. The elevation ranges from 1140 to 2562 m above sea level and the area extends from 08°00′42′’ to 08°44′23′′ N and 35°20′31′′ to 36°18′20′′ E (Gole et al. 2003). The annual temperature varies between 12.7 °C and 26.1 °C on average, and the mean annual precipitation is 2100 mm, oscillating from year to year from 1400 to 3000 mm (Gole et al. 2008).

Comprising 167,000 ha and about 320,000 inhabitants (CSA 2007), the Yayu area overlaps with the Yayu Coffee Forest Biosphere Reserve established by UNESCO in 2011 (Fig. 1). This is one of the last remaining montane rainforests containing wild Coffea Arabica (Gole et al. 2009). Hence, it plays a significant role in natural and cultural conservation, and also for the local economy. Yayu rural households depend greatly on coffee cultivation. More than 60% of the population depends financially on coffee production and coffee-related activities, such as its collection, processing and trade (Gole et al. 2008). Other predominant crops are khat (Catha edulis), maize (Zea mays), sorghum (Sorghum bicolor) and tef (Eragrostis tef).

Fig. 1
figure1

Source: Adapted by the Authors from Gole et al. (2009)

Location of the Yayu Coffee Forest Biosphere Reserve;

Fig. 2
figure2

Process of selection of underutilized edible species

Species identification, selection and sampling

This research was a subset of a major study on the roles of agroforestry systems on human nutrition. Data collection applied a multistage systematic sampling. The proximity of a household to the forest (core biosphere reserve) and market (urban agglomeration) were the extremes that defined the sampling sites. Accordingly, eight sites/Kebeles (lowest administrative unit) in four Woredas (district-equivalent) were selected (Callo-Concha et al. 2019; Jemal et al. 2018). Three hundred households (n = 300) were randomly selected, and an ethnobotanical survey implemented to identify and document all edible plant species, and the householders’ practices, opinions, perceptions and preferences towards these. Three successive subsettings were implemented, considering: (i) all useful species growing in agroforestry plots, (ii) all edible species, by consulting knowledgeable individuals, and (iii) the species available at the time of the sampling (seasonal availability) (Jemal 2018).

Key informants (n = 40), were interviewed to identify the species usefulness and widespread cultivation. Field assessments, guided by local agronomists and botanists, were conducted to identify and characterize the species in the field. This has helped us to validate the preferences of the interviewees and document the most liked ones. We also contrasted our list with a specialized database (Fern and Fern 2014), to refine the information accuracy. In the case of unknown species, a voucher specimen was taken to the National Herbarium of Ethiopia for final identification. From the general interviews, the 12 most commonly recalled were selected for further analyses (see Table 1).

Table 1 Characterization of the 12 shortlisted edible plant species

Although the main goal was to identify wild edible plants and analyze their biochemical content that determine the nutritional quality, we also collected some socioeconomic information, which included the species current use status, mode of preparation and consumption, type of management, and other uses.

Nutrient content analyses

Sample preparation

In the field, samples of about 500 g of main edible parts, e.g., leaf, stem, tuber, root or fruits, were stored in an icebox to be transported to the laboratory. Leaf samples were washed and chopped to a uniform size. Tubers were peeled, washed and cut into small pieces, which later were pulverized. Fruit pulp was washed and separated from the seeds. These were oven-dried at 60 °C until reaching constant weight, and grounded to fine powder. Samples were then labelled in plastic bags and stored at room temperature. Similarly, depending on the analyses, all freshly prepared samples were labelled and stored in a deep freezer (−20 °C). Proximate food composition, vitamins and antinutritional factors analysis was performed at Jimma University, Ethiopia, and the minerals content was analyzed at the University of Bonn, Germany.

Minerals and vitamins content determination.

The mineral concentrations were determined in accordance with the methods of the Association of Official Analytical Chemists (AOAC 2003). The total beta-carotene content was determined by spectrophotometry using the method described by Sadler et al. (1990) with a few modifications. Ten gram of the samples were placed in a 125-ml flask, and 100 ml of hexane–acetone-ethanol (50:25:25), and extraction solvent containing 0.1% BHT was added to the flask. This was wrapped in aluminium foil and agitated for 10 min on a wrist action homogenizer (PLTYRON®2500E, Switzerland). The solution was then mixed with 1 g CaCl2.2H2O and gently shaken for 30 min by a mechanical shaker. After adding 15 ml distilled H2O, the solution was shaken again for 15 min. The organic phase containing beta-carotene was separated from the water phase using a separation funnel and filtered through 0.45-µm membrane filters.

Sample handling, homogenization and extraction were performed under low light and at 4 °C to minimize photo-isomerization and oxidation of carotenoids. Each sample was analyzed three times (n = 36) and an average value calculated. The beta-carotene content in the sample and beta-carotene standard (Sigma Aldrich) were estimated from absorbance read at 450 nm using spectrophotometry (UV–Vis spectrophotometer, T80 China). The beta-carotene content was calculated using a regression equation after the analysis of the standard curve and expressed as µg RAE per 100 g edible portion. Vitamin C content was determined by iodometric titration using the method described by Sowa and Kondo (2003).

Antinutritional factors content determination

The colorimetric assay of phytate was determined using spectrophotometry following the method applied by Vaintraub and Lapteva (Vaintraub and Lapteva 1988). Tannin was determined using spectrophotometry based on the Maxson and Rooney method (Maxson and Rooney 1972). The oxalate content was determined with permanganate titration as described in the method (Ukpabi and Ejidoh 1989).

Data analysis

Each experiment was executed in triplicate. Descriptive statistics for mean values and standard errors were calculated for minerals, vitamins and antinutritional factors content determination and comparison. One-way analysis of variance (ANOVA) and t-test were applied, and the least significance differences (LSD) post-hoc test implemented to compare the means. Calculations were done by the R-software, specifically by the agricolae package (Free Software Foundation Inc. USA).

Results and discussion

Underutilized edible species

Ninety-four (94) edible plant species were identified and their use documented. They belong to 79 genera and 41 families. The most abundant genera are Moraceae and Rutaceae (8 species each), Poaceae (7), Fabaceae (6), Solanaceae (5), Brassicaceae and Rosaceae (4 species each) and Dioscoraceae, Zingiberaceae and Meliaceae (3 species each).

It was recorded that most of the 94 species identified, are casually picked and consumed mostly while doing agricultural and forestry-related and by searching for traditional medicines. In lesser extent when community members enter to the forest for purposes such as collecting materials for farm tools, preparing charcoal, gathering construction materials and hunting. However, they also reported a current decrease in collection of forest foodstuff, which does not mean an abandonment but rather tells on their importance as repository during shortage of other agricultural products: ‘This forest [Yayu] is our food bank, whenever necessary I go to the forest and collect fruit for myself and family, so I keep on watching the forest’ (Kochina Geba Village, 30/05/2016). However, it was also pointed out that the rapid conversion of forest to farmland and the decreasing productivity of forests poses challenges to local peoples, thus some of them have started to collect some of these species and transplanted in their home gardens. Another common practice is to purposefully leave some edible species, for instance regarding valuable trees species that provide shade but also produce fruits.

From a list of preferred 25 edible species, either under cultivation or (semi)domesticated, the 12 available during the study period were taken for nutritional analysis. The 12 shortlisted species belong to fruits, vegetables and roots and are consumed as fruit, leaf and tuber, respectively. Fruits are found in agroforestry multistorey systems, while vegetables and roots mostly occur in homegardens and the later receives occasional management (Table 1).

Green leafy vegetables grow in a large part of southwestern Ethiopia during the rainy season, and often are consumed to help to bridge the food shortage gap when the staple crops are not yet harvested (Uusiku et al. 2010). That is the case of Amaranthus graecizans, Solanum nigrum, Hypolepis sparsisora and Portulaca quadrifida, that are mostly available between July and September, and therefore are called “ye kiremt migboch” (summer foods in Amharic language) (Stellmacher and Kelboro 2015); although may also be cultivated during the dry season through supplemental irrigation (Senbeta et al. 2010). Fruits and tubers, on the other hand, are abundant in the dry season, when are consumed raw and sometimes processed, e.g. as juices. In terms of management, fruits such as Carissa spinarum and Syzygium guineense are not cultivated regularly but collected instead. Tubers like Disocorea prehensilis, a wild yam growing in the understory of coffee forests, has not been widely acknowledged as food stuff, but we have found to be rich in key nutrients. Still, most of these species are also consumed in other parts of the country. For example, edible fruit bearing species such as Ficus sycomorus and Syzygium guineense in Derashe and Kucha districts of southern Ethiopia (Balemie and Kebebew 2006).

Energy and micronutrients

The leaves of Amaranthus graecizans, Hypolepis sparsisora, Portulaca oleracea and Solanum nigrum hold the highest content of protein: 17.95, 18.43, 15.62 and 19.26 g/100 g dry EP, respectively. Similar results have been reported for other green leafy vegetables in other parts of Africa. For instance, the amount of protein obtained in Amaranthus gaecizans is comparable with values reported from Mali and northern Senegal, that range from 17.92 to 23.2 g/100 g dry EP (Becker 1983; Akubugwo et al. 2007). In addition, Venskutonis and Kraujalis (2013), have conducted an extensive review on Amaranthus spp and found out that its protein content in leaves vary from 14 to 30 g/kg FW g in the wild, and among cultivars, values that are consistent with our results.

The identified green leafy vegetables were also rich in Ca, Fe and Zn. A. graecizans (2065 mg/100 g dry EP) had the highest Ca content, while S. guineense the lowest (65 mg/100 g dry EP). Values in the remaining species varied in the range of 75–1225 mg/100 g dry EP. Similarly, Fe and Zn contents varied significantly among the fruit- and leafy vegetable-provider species (p ≤ 0.05), but the Fe content was higher in leafy vegetables and tubers. The highest Fe content was found in A. graecizans (91.29 mg/100 g dry EP) followed by D. cayenensis (46.78 mg/100 g dry EP) and P. oleracea (44.51 mg/100 g dry EP). Furthermore, we found significantly high amounts of Zn (6.51 and 4.33 mg/100 g dry EP) in R. apetalus and P. oleracea, respectively (Table 2).

Table 2 Minerals, Vitamins and Antinutritional factors content of 12 edible plant species (per 100 g EP)

A precedent study showed that mature leaves of P. oleracea contain particularly high amounts of Ca, Fe and Zn (Uddin et al. 2012), and also omega-3 fatty acid, α-tocopherol, ascorbic acid, β-carotene and glutathione are abundant in shoots (Wenzel et al. 1990), considering it a source of minerals, vitamins and antioxidants for functional foods and nutraceutical applications (Wenzel et al. 1990). This evidence suggests, that the consumption of A. graecizans D. cayenensis and P. oleracea could substantially address the persistent iron deficiency in the Yayu, where 96.4% of women at productive age lack in their diets during shortage season (Jemal 2018).

The beta-carotene content varied significantly among species, in the range of 110 – 1940 µg/100 g fresh EP (9.2 – 161.67 µg RAE /100 g fresh EP, considering the latest conversion factor). The species with the highest content was R. apetalus (161.67 µg RAE/100 g fresh EP), likely associated with its yellow pigment (as we applied the spectrophotometric method, there is a limitation in differentiating beta-carotene from other carotenoids and chlorophyll). Hence, we have estimated that 100 g of R. apetalus can provide nearly 50% of the daily recommended vitamin A required by children, 23% to female adults and 21% to pregnant women of the recommended dietary intake. Similarly, 100 g of fresh leaves of A. graecizans (75 µg RAE/100 g EP) would contribute 20% of the recommended intake of vitamin A for children, 13% for females, and 11% for pregnant women (NIH 2018).

The vitamin C content also varied significantly among species in the range between 126.88 and 330.72 mg/100 g fresh EP, being higher in the fruits of S. guineense (330.72 mg/100 g fresh EP) and R. apetalus (294.19 mg/100 g fresh EP), and in A. graecizans (Table 2). The obtained values agree with those reported for sub-Saharan Africa and India (Stadlmayr et al. 2013). In the case of tubers of D. cayenensis and D. prehensilis, although their vitamin C content is high, their dietary contribution is difficult to calculate, as vitamin C content is greatly affected by temperature (Hernández et al. 2006). In this line, reductions in vitamin C due to cooking have been reported in Amaranthus spp. (65%), dried V. amygdalina (61%), and almost 100% in dried A. digitate (Yadav and Sehgal 1995; FAO 1990).

Antinutritional factors

Antinutritional factors are compounds intrinsic to the composition of species that limit the utilization of nutrients by humans and animals that consume them (Soetan and Oyewole 2007). High phytate content inhibits the bioavailability of minerals (FAO and WHO 2001). In the shortlisted species, the phytic acid content varied significantly from 31.06 μg/100 g fresh EP (D. prehensilis) to 601.65 μg/100 g fresh EP (C. spinarum). Values were especially low in tubers: D. alata, D. cayenensis and D. prehensilis, whose content ranged between 31.06 and 96.48 µg per 100 g fresh EP (Table 2). These values are lower to the ones reported in Nepal for similar species (Wanasundera and Ravindran 1994). Similarly, the phytate content in S. nigrum (536 µg/100 g EP) are slightly lower compared than the values obtained in a similar study conducted in Nigeria (Akubugwo et al. 2007). As Ca and phytates determine the bio-availability and absorption of Fe. The benefits of iron-rich green vegetables and fruits in preventing anaemia depend not only on the intake itself, but also on the presence of ascorbic acid, which contributes to its absorption. According to the daily recommended calcium intake for all age groups (800–1200 mg), a 50 g of fresh leaves of Amaranthus could provide a daily Ca requirement.

Tannins are also undesirable in high levels, as by interacting with proteins, starch and digestive enzymes, reduce the nutritional value of foods (Chung et al. 1998). Tannins content was the highest in the fruits of S. guineense (3.97 mg/100 g fresh EP) followed by F. sycomorus (1.96 mg/g fresh EP). However, out of the 12 species analysed, in 5 species no tannins were detected, but in the other 7 the content varied significantly (p < 0.05) from 3.15 mg/ g EP (T. mauritianum) to 3.97 mg/ g fresh EP (S. guineense) (Table 2). These low values might also be consequence of the freezing, as long freezing periods were reported to reduce the tannin content in some vegetables (Aregahegn et al. 2013). Its value in C. spinarum (1.31 mg/g 100 g fresh EP) was consistent with Ambika et al. (2015).

The oxalate content also varied significantly (p < 0.05) from 0.84 – 4.22 mg/100 g fresh EP, the highest were found in the leaves of A. graecizans and the fruits of C. spinarum (Table 2). In the case of Dioscorea spp. (2.46—2.81 mg/100 g), was found to be lower compared to values in other reports (Wanasundera and Ravindran 1994; Bhandari and Kawabata 2004). However, variations in oxalates content differ by cultivar, planting and harvesting conditions; and it is also known that their detection may vary depending on the analytical techniques applied. Nevertheless, all green vegetables and tubers analysed are consumed cooked, which reduces the levels of phytates, tannins and oxalates. For example, S. nigrum loses its bitter taste after cooking (personal experience).

Finally, Ca, Fe and Zn contents, as well as the calorific value, were the proxies used to compare the nutritional potential of underutilized species against commonly cultivated crop species. Almost all green vegetables identified provide significantly less energy compared to popular crops species like tef (Eragrostis tef), maize (Zea mays), sorghum (Sorghum bicolor), bean (Phaseolus vulgaris L.) and enset (Ensete ventricosum), with the exception of yam (D. cayenensis), whose energy values are similar to tef, maize and enset. However, regarding protein, mineral and vitamin contents, the species analysed have shown higher values compared to the species commonly consumed. Some underutilized species showed up to tenfold higher content of Ca, as it is the case of the leaves of A. graecizans, when compared to tef seeds. Similarly, Portulaca oleracea is considered a weed plant by many people in Ethiopia, but its leaves and stems contain high amounts of Fe, Zn and vitamin C, e.g. twice the amount of Fe in maize. Indigenous fruits such as C. spinarum and S. guineense were observed to provide higher energy values than commonly consumed exotic species, such as mango (Mangifera indica) and papaya (Carica papaya).

In Jemal (2018) assessment of Yayu rural householders’ diets, iron happened to be the most critical nutrient, notably low in women in reproductive age and children under five years old; furthermore, the situation tends to worsen in the food scarcity seasons, leading to potential chronic deficiencies (Jemal 2018). Such a situation is not exclusive to Yayu, but reported country wide (CSA and WFP 2014). Our findings state that in terms of vitamin provisions some of the underutilized plants can be a promising alternative, for example R. apetalus, capable to hold up to 10 times more beta-carotene than mango (Table 3).

Table 3 Nutrient content values of the identified underutilized species against values of popular crop species in Yayu per 100 g dry edible portion

Conclusions

It is documented that most households in Yayu face food shortages during the rainy season (June–August). We stand that the detected underutilized species can contribute to bridging this food shortages gap, and some of them, like fruits produced during the dry season (January-April), also can help to improve the overall quality of householder diets.

Among the found species, leafy vegetables, such as Amaranthus graecizans, Portulaca oleracea and Solanum nigrum, have proved to be good sources of protein and minerals (Ca, Fe and Zn). While other species were reported to be good sources of pro-vitamin A (Rubus apetalus) and vitamin C (Syzygium guineense), at the same time that contain relatively low amounts of antinutritional factors. Furthermore, it was found that the nutritional values of the analysed species is comparable and sometimes higher than the ones of conventionally cultivated crops, e.g. Portulaca oleracea provides more dietary Fe than maize.

This study shows that an increase in the food and nutrition standards of Yayu inhabitants are feasible and, more importantly, depends almost exclusively of the householders themselves. However, the use of these underutilized edible species require of additional research and development. Key aspects include: harvesting, postharvest processing, storage, preparation, bioavailability and marketing, not only to improve the food safety and quality, but also to minimize waste and promote their effective and sustainable use.

References

  1. Akubugwo IE, Obasi AN, Ginika SC (2007) Nutritional Potential of the Leaves and Seeds of Black NightshadeSolanum nigrum L. Var virginicum from Afikpo-Nigeria. Pakistan J Nutrition. 6(4):323–326

    Article  Google Scholar 

  2. Ambika C, Beenu T, Intelli A (2015) Influence of processing on physiochemical, nutritional and phytochemical composition of Carissa spinarum (karonda) fruit. Asian J Pharm Clin Res 8(6):254–259

    Google Scholar 

  3. Aregahegn A, Chandravanshi B, Atlabachew M (2013) Levels of major, minor and toxic metals in tubers and flour of Dioscorea abyssinica grown in Ethiopia. ajfan (Afr J Food Agric Nutr Dev 13(3):7870–7887

    CAS  Google Scholar 

  4. Association of Analytical Chemists (AOAC) (2003) Official Methods of Analysis. 17th ed. Washington, DC. Association of Official Analytical Chemist; Method number 942.5. http://www.eoma.aoac.org/methods/info.asp?ID=15499. Accessed 25 May 2020

  5. Balemie K, Kebebew F (2006) Ethnobotanical study of wild edible plants in Derashe and Kucha Districts, South Ethiopia. J Ethnobiol Ethnomed 2006:9

    Google Scholar 

  6. Baye K, Hirvonen K, Dereje M, Remans R (2019) Energy and nutrient production in Ethiopia, 2011–2015: Implications to supporting healthy diets and food systems. PLoS ONE 14(3):e0213182. https://doi.org/10.1371/journal.pone.0213182

    CAS  Article  PubMed  PubMed Central  Google Scholar 

  7. Becker B (1983) The contribution of wild plants to human nutrition in the Ferlo (Northern Senegal). Agroforest Syst 1(3):257–267. https://doi.org/10.1007/BF00130611

    Article  Google Scholar 

  8. Belcher B, Ruíz-Pérez M, Achdiawan R (2005) Global patterns and trends in the use and management of commercial NTFPs: Implications for livelihoods and conservation. World Dev 33(9):1435–1452. https://doi.org/10.1016/j.worlddev.2004.10.007

    Article  Google Scholar 

  9. Beyero M, Hodge J, Lewis A (2015) Leveraging Agriculture for Nutrition in East Africa (LANEA): Country Report-Ethiopia. Food and Agriculture Organization of the United Nations (FAO) & International Food Policy Research Institute (IFPRI)

  10. Bhandari MR, Kawabata J (2004) Assessment of antinutritional factors and bioavailability of calcium and zinc in wild yam (Dioscorea spp.) tubers of Nepal. Food Chem 85(2):281–287. https://doi.org/10.1016/j.foodchem.2003.07.006

    CAS  Article  Google Scholar 

  11. Bharucha Z, Pretty J (2010) The roles and values of wild foods in agricultural systems. Phil Trans Royal Soc B: Biol Sci 365(1554):2913–2926. https://doi.org/10.1098/rstb.2010.0123

    Article  Google Scholar 

  12. Callo-Concha D, Mohamed O, Seyoum Aragaw H (2019) Local alternatives to local problems: the contribution of agroforestry system by-products to food and nutrition security of communities in Southwestern Ethiopia. Food Stud: An Interdiscip J 9(1):29–42. https://doi.org/10.18848/2160-1933/cgp/v09i01/29-42

    Article  Google Scholar 

  13. Centeral Statistic Agency (CSA) [Ethiopia] (2007) Population and housing census of oromia regional state: Federal Democratic Republic of Ethiopia. Addis Ababa, Ethiopia

  14. Centeral Statistic Agency (CSA) [Ethiopia] and ICF International. Ethiopian Demographic and Health Survey (2016) Key Indicators Report. Addis Ababa, Ethiopia, and Rockville, Maryland, USA. dhsprogram.com/pubs/pdf/SR241/SR241.pdf

  15. Cernansky R (2015) The rise of Africa’s super vegetables. Nature News 522(7555):146

    CAS  Article  Google Scholar 

  16. Chung K-T, Wong TY, Wei C-I, Huang Y-W, Lin Y (1998) Tannins and Human Health: A Review. Critical Rev Food Sci Nutr 38(6):421–464. https://doi.org/10.1080/10408699891274273

    CAS  Article  Google Scholar 

  17. CSA (Central Statistical Agency), WFP (2014) Comprehensive Food Security and Vulnerability Analysis (CFSVA): Ethiopia. Available via http://documents.wfp.org/stellent/groups/public/documents/ena/wfp265490. Accessed 12 May 2020

  18. Fentahun MT, Hager H (2009) Exploiting locally available resources for food and nutritional security enhancement: wild fruits diversity, potential and state of exploitation in the Amhara region of Ethiopia. Food Sec 1(2):207–219. https://doi.org/10.1007/s12571-009-0017-z

    Article  Google Scholar 

  19. Fern K, Fern A (2014) Useful tropical plants database. http://tropical.theferns.info/. Published 2014

  20. Food and Agriculture Organization of the United Nations (FAO) (1990) Utilization of tropical foods: fruits and leaves. FAO, Food and Nutrition Paper No 47/7. 1990

  21. Food and Agricultural Organization (FAO) & Ethiopian Health Nutrition Research Institute (EHNRI) (1998) Food Composition Table for Use in Ethiopia. Vol IV. Addis Ababa, Ethiopia: Food and Agriculture Organization of the United Nations (FAO)

  22. Food and Agriculture Organization of the United Nations (FAO) and World Health Organization (WHO) (2001) Human Vitamin and Mineral Requirements: Report of a Joint FAO/WHO Expert Consultation, Bangkok, Thailand. Rome: Food and Agriculture Organization of the United Nations (FAO)

  23. Food and Agriculture Organization of the United Nations (FAO) (2017) Nutrition-Sensitive Agriculture and Food Systems in Practice: Options for Intervention. Rome: Food and Agriculture Organization of the United Nations (FAO)

  24. Frison E. and Padulosi S (1999) The Role of Underutilized Plant Species in the 21 St Century. Global Forum on Agricultural Research. Aleppo, Syria: IPGRI; 1–7

  25. Gole TW, Denich M, Martius C, Giesen Ni van de, Vlek PLG (2003) Vegetation of the Yayu forest in SW Ethiopia: impacts of human use and implications for in situ conservation of wild coffea arabica L. populations. https://cuvillier.de/uploads/preview/public_file/6946/3898738663.pdf

  26. Gole TW, Borsch T, Denich M, Teketay D (2008) Floristic composition and environmental factors characterizing coffee forests in southwest Ethiopia. Forest Ecol Manag 255:2138–2150. https://doi.org/10.1016/j.foreco.2007.12.028

    Article  Google Scholar 

  27. Gole TW, Senbeta F, Tesfaye K, Getaneh F (2009) Yayu Coffee Biosphere Reserve Nomination Forum. Ethiopian MAB National Committee, Addis Ababa. https://www.cbd.int/database/attachment/?id=556

  28. Grivetti LE, Ogle BM (2000) Value of traditional foods in meeting macro- and micronutrient needs: the wild plant connection. Nutri Res Rev. 13(01):31. https://doi.org/10.1079/095442200108728990

    CAS  Article  Google Scholar 

  29. Hernández Y, Lobo MG, González M (2006) Determination of vitamin C in tropical fruits: A comparative evaluation of methods. Food Chem. 96(4):654–664. https://doi.org/10.1016/j.foodchem.2005.04.012

    CAS  Article  Google Scholar 

  30. Jemal O (2018) The role of local agroforestry practices for enhancing food and nutrition security of smallholding farming households: The case of Yayu Area, Southwestern Ethiopia. PhD Thesis

  31. Jemal O, Callo-Concha D, van Noordwijk M (2018) Local Agroforestry Practices for Food and Nutrition Security of Smallholder Farm Households in Southwestern Ethiopia. Sustainability. 10(8):2722. https://doi.org/10.3390/su10082722

    Article  Google Scholar 

  32. Khoury CK, Bjorkman AD, Dempewolf H et al (2014) Increasing homogeneity in global food supplies and the implications for food security. Proc National Acad Sci 111(11):4001–4006. https://doi.org/10.1073/pnas.1313490111

    CAS  Article  Google Scholar 

  33. Lulekal E, Asfaw Z, Kelbessa E, Van Damme P (2011) Wild edible plants in Ethiopia: a review on their potential to combat food insecurity. Afrika Focus 24(2). doi:https://doi.org/10.21825/af.v24i2.4998

  34. Maxson ED, Rooney LW (1972) Evaluation of methods for tannin analysis in Sorghum grain. Am Assoc Cereal Chem 1972:49

    Google Scholar 

  35. National Institute of Health (NIH) (2018) Department of Health and Health Service - National Institute of Health (NIH). Vitamin A-Fact sheet for health professionals. Vitamin A-Fact sheet for health professionals. https://ods.od.nih.gov/factsheets/VitaminA. Accessed 14 April 2019

  36. Padulosi S, Thompson J, Rudebjer P (2013) Fighting poverty, hunger and malnutrition with neglected and underutilized species (NUS): needs, challenges and the way forward. Biodiversity International, Rome

    Google Scholar 

  37. Pimentel PDD, Pimentel MSMH (2007) Food, Energy, and Society, Third Edition; http://ebookcentral.proquest.com/lib/qut/detail.action?docID=313446

  38. Pol JLV (2002) Forest is not only wood: The importance of non-wood forest products for the food security of rural households in Ethiopia. In: Demel T, Yonas Y (eds.) “Forests and Environment,” Proceedings of the fourth annual conference of forestry society of ethiopia. addis ababa, Ethiopia: Forestry Society of Ethiopia

  39. Powell B, Thilsted SH, Ickowitz A, Termote C, Sunderland T, Herforth A (2015) Improving diets with wild and cultivated biodiversity from across the landscape. Food Sec 7(3):535–554. https://doi.org/10.1007/s12571-015-0466-5

    Article  Google Scholar 

  40. Sadler G, Davis J, Dezman D (1990) Rapid extraction of lycopene and ?-Carotene from reconstituted tomato paste and pink grapefruit homogenates. J Food Sci 55(5):1460–1461. https://doi.org/10.1111/j.1365-2621.1990.tb03958.x

    CAS  Article  Google Scholar 

  41. Sena LP, Vanderjagt DJ, Rivera C, et al. (1998) Analysis of nutritional components of eight famine foods of the Republic of Niger. Plant Foods Hum Nutr 52:17–30. https://doi.org/10.1023/A:1008010009170

  42. Senbeta F, Machlachlan M, Bekele M, Barklund P (2010) Edible Wild Plants in Ethiopia. Vol 575. Teketay D. Addis Ababa. Addis Ababa University Press, Ethiopia

    Google Scholar 

  43. Seyoum Keflie T, Samuel A, Lambert C, Nohr D, Biesalski HK (2018) Dietary Patterns and Risk of Micronutrient Deficiencies: their Implication for Nutritional Intervention in Ethiopia. J Nutr Health Food Sci 6(1):1–16. https://doi.org/10.15226/jnhfs.2018.001120

    Article  Google Scholar 

  44. Sheehy T, Carey E, Sharma S et al (2019) (2019) Trends in energy and nutrient supply in Ethiopia: a perspective from FAO food balance sheets. Nutr J 18:46. https://doi.org/10.1186/s12937-019-0471-1

    CAS  Article  PubMed  PubMed Central  Google Scholar 

  45. Soetan KO, Oyewole OE (2007) The need for adequate processing to reduce the antinutritional factors in plants used as human foods and animal feeds: A review. Af J F S. 3(9):223–232

    Google Scholar 

  46. Sowa S, Kondo AK (2003) Sailing on the “C”: A Vitamin Titration with a Twist. J Chem Edu 80(5):550

    CAS  Article  Google Scholar 

  47. Stadlmayr B, Charrondière UR, Eisenwagen S, Jamnadass R, Kehlenbeck K (2013) Nutrient composition of selected indigenous fruits from sub-Saharan Africa: Nutrient composition of selected indigenous fruits from sub-Saharan Africa. J Sci Food Agric 93(11):2627–2636. https://doi.org/10.1002/jsfa.6196

    CAS  Article  Google Scholar 

  48. Stellmacher T, Keboro G (2015) Local dynamics and perceptions of food insecurity among AgroForestry Family Farms in Ethiopia. In: Eric Tielkes (ed). Management of land use systems for enhanced food security: conflicts, controversies and resolutions. Berlin, Germany

  49. Tulu ZJ (2010) Institutions, incentives and conflict in coffee forest use and conservation: the case of Yayu Forest in Iluu Abba Bora Zone, Southwest Ethiopia. hss.ulb.uni-bonn.de/2010/2160/2160.pdf

  50. Uddin MdK, Juraimi AS, Ali MdE, Ismail MR (2012) Evaluation of antioxidant properties and mineral composition of purslane (Portulaca oleracea L.) at different growth stages. Int J Molecular Sci 13(8):10257–10267. https://doi.org/10.3390/ijms130810257

    CAS  Article  Google Scholar 

  51. Ukpabi U, Ejidoh J (1989) Effect of deep oil frying on the oxalate content and the degree of itching of coco yams (Xanthosoma and Colocasia spp). Owerri. Federal University of Technology, Nigeria, pp 3–9

    Google Scholar 

  52. United States Department of Agricultural Research Service (USDA) (2018) Food Composition Databases. National Nutrient Database for Standard Reference Release 28. USDA Food Composition Databases. https://ndb.nal.usda.gov/ndb/search/list. Accessed 19 August 2018

  53. Uusiku NP, Oelofse A, Duodu KG, Bester MJ, Faber M (2010) Nutritional value of leafy vegetables of subSaharan Africa and their potential contribution to human health: A review. J Food Comp Anal 23(6):499–509. https://doi.org/10.1016/j.jfca.2010.05.002

    CAS  Article  Google Scholar 

  54. Vaintraub IA, Lapteva NA (1988) Colorimetric determination of phytate in unpurified extracts of seeds and the products of their processing. Anal Biochem 175(1):227–230. https://doi.org/10.1016/0003-2697(88)90382-x

    CAS  Article  PubMed  Google Scholar 

  55. Venskutonis PR, Kraujalis P (2013) Nutritional components of amaranth seeds and vegetables: A review on composition, properties, and uses: Nutritional components of amaranth seeds and vegetables. Compr Rev Food Sci Food Safety. 12(4):381–412. https://doi.org/10.1111/1541-4337.12021

    CAS  Article  Google Scholar 

  56. Wanasundera JPD, Ravindran G (1994) Nutritional assessment of yam Dioscorea alata tubers. Plant Food Human Nutrition 46(1):33–39. https://doi.org/10.1007/BF01088459

    CAS  Article  Google Scholar 

  57. Wenzel GE, Fontana JD, Correa JBC (1990) The viscous mucilage from the weed Portulaca oleracea L. Appl Biochem Biotechnol 24–25(1):341–353. https://doi.org/10.1007/BF02920258

    Article  Google Scholar 

  58. Yadav SK, Sehgal S (1995) Effect of home processing on ascorbic acid and -carotene content of spinach Spinacia oleracia and amaranth Amaranthus tricolor leaves. Plant Foods Human Nutr 47(2):125–131. https://doi.org/10.1007/BF01089261

    CAS  Article  Google Scholar 

Download references

Acknowledgements

We are greatly indebted to Dr. Omarsherif Jemal., Mr. Matewos Bekele, Mr. Dessie Olana for their cooperation during data collection. We thank Dr. Julian P. Wald for his support during the laboratory analysis. We thank also the ECFF (Environment and Coffee Forest Forum) and the Agricultural offices of Yayu and the surrounding Woreda—their support and facilitation were indispensable for realization of the field work. We also extend our sincere thanks to Ms. Margaret Jend for editing this manuscript.

Funding

Open Access funding enabled and organized by Projekt DEAL. This research was part of the project BiomassWeb—Improving food security in Africa through increased system productivity of biomass-based value webs funded by the German Federal Ministries of Education and Research (BMBF) and of Cooperation and Development (BMZ), grant number FKZ 031 A258 A.

Author information

Affiliations

Authors

Contributions

Conceptualization, H.S.A., D. N & D.C.C., field work, analysis, drafting, H.S.A.; review and editing, H.S.A., D.N., & D.C.C.

Corresponding author

Correspondence to Habtamu Seyoum Aragaw.

Ethics declarations

Conflicts of interest

The authors have declared no conflict of interest.

Additional information

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Aragaw, H.S., Nohr, D. & Callo-Concha, D. Nutritional potential of underutilized edible plant species in coffee agroforestry systems of Yayu, southwestern Ethiopia. Agroforest Syst 95, 1047–1059 (2021). https://doi.org/10.1007/s10457-021-00626-6

Download citation

Keywords

  • Diet diversity
  • Underutilized food plants
  • Nutritional potential
  • Antinutritional factors