- Open Access
“A herder’s duty is to think”: landscape partitioning and folk habitats of Mongolian herders in a mountain forest steppe (Khuvsugul-Murun region)
Journal of Ethnobiology and Ethnomedicine volume 15, Article number: 54 (2019)
Traditional habitat knowledge, like the classification of folk habitats and how people partition their landscape into habitats, is an emerging but still understudied part of traditional ecological knowledge. Our objectives were to reconstruct the folk habitats and the partitioning of the landscape into these folk habitats by Mongolian herders in Northern Mongolia and to compare it with other Northern Hemisphere boreal-temperate classifications.
The study area is located in Seruun Gilad (Khuvsugul province) and belongs to the mountain forest steppe of the Khangai region (dominated by meadow steppes and larch forests). Most herder families use the area for summer pasturing. Data collection was based on indoor and outdoor, structured and semi-structured interviews and interviews during landscape walks and participatory fieldwork. We interviewed 20 people using 76+ photos of plant species and 25+ photos of habitats and asked them to name and describe the habitats and describe the habitat preferences of the species.
Mongolian herders distinguished at least 88 folk habitat categories and knew well the habitat preferences of the 76 plant species. They argued that a herder has to be observant of nature. The habitat classification was moderately lexicalized, with many descriptive expressions. Most habitats (77%) belonged to the meso-scale, while macro-scale habitats (like taiga, Gobi) and micro-scale habitats (like marmot burrow, top of the tussock) were few. Habitat names did not reflect directly the usefulness of the habitat. Classification was multidimensional; key dimensions were geomorphological and edaphic. There were some species (e.g., botyuul, hyag, shireg) and species groups (hot plants, leafy plants) that were often used to describe habitat types.
Landscape partitionings in the Northern Hemisphere differed considerably in the importance of various dimensions used, with edaphic, geomorphological, hydrological, and dominant species-based dimensions having higher importance, while land use, successional, and zoological dimensions having lower importance. We argue that conducting research on folk habitats will contribute to a deeper understanding of how nature is perceived by locals and to a more efficient management of the Mongolian pastures.
Sustainable use of natural resources demands a deep understanding of the managed ecosystems . For example, rangelands utilized by nomadic, transhumant, or sedentary herders may degrade if governance and management are not adapted to the carrying capacity of the forage resources [2,3,4,5]. Traditional pastoral communities all over the world have a long-term, place-based understanding of the spatio-temporal patterns of their pasture resources (e.g., [6,7,8,9]). This knowledge is dynamic and has been transmitted through generations and adapted to changing socio-ecological conditions . A significant part of this knowledge refers to the living components of the local environment pastoralists live in.
Ethnobiologists seek to understand how different human communities perceive, classify, and mentally process the living world and how people then apply that knowledge . This knowledge is often called traditional ecological knowledge . Ethnobiologists have traditionally focused on the folk classification and traditional use of plants and animals . In the last decades, more and more studies are available on the habitat and vegetation-related traditional knowledge of local traditional communities, including herders, farmers, fishers, and hunters (e.g., [13,14,15,16]). Johnson and Hunn  introduced the term landscape ethnoecology which focuses on the ecological features of a landscape (e.g., ecotopes, habitats, vegetation types, and other landscape elements) and aims to understand how the living landscape is perceived, named, imagined, classified, and managed by people who live in it. Landscape elements, including habitat patches, are generally less discrete elements of the environment than plant and animal individuals. However, locals have a deep knowledge of these landscape elements including their characteristic species, structure, and function. In case of habitats, only variants exist in nature, which can be arranged along continua and around prototypes in classifications (, sensu ). Landscape elements have a diverse terminology in ethnobiology: ecotope, habitat, kind of place, and biotope . We follow Molnár  and use the term habitat that includes all living creatures on a piece of land with its soil, bedrock, and hydrology. A habitat is mostly defined by its vegetation and soil and is more or less a synonym of ecotope.
Evidence shows that people in traditional communities tend to distinguish many habitats in a landscape; the average number of basic-level categories seems to be around 25 , whereas synonymous names are not rare. Locals distinguish habitats at different spatial scales. While folk plant classifications are most often strongly hierarchical , folk habitat types are usually ordered into less hierarchical partitionings and are often multidimensional . A landscape partitioning is multidimensional if the partitioning uses several distinct sets of salient environmental features to define habitats, and habitats cannot be arranged in a unidimensional system (cf. ).
Whereas traditional ecological knowledge of African pastoralist communities is well-documented (e.g., [6, 8, 23,24,25,26]), herder communities in northern regions are less often studied. One of the most famous groups of pastoralists is the nomadic and semi-nomadic Mongolian pastoralists. The herding tradition of Inner-Asian nomads dates back at least 3000 years . Nomadic knowledge of nature is passed on from generation to generation but adapted to the changing conditions [3, 28]. Herder families still practice many old traditions, including using yurts (ger in Mongolian) and utilize pastures in a seasonal rotation to avoid overgrazing . Roughly 30% of Mongolians are pastoralists, and at least half of the Mongolians still depend on the pastoral economy for their livelihood . Mongolian herders use their traditional ecological knowledge of seasonal changes, dynamics of pastures, etc. to determine the grazing areas they will move to. This understanding of nature is especially important during the extreme winter conditions (dzud), which can kill many of their animals [30, 31]. Mongolians possess a detailed knowledge of pasture forage species [32, 33] and pasture degradation [34, 35] but also have a rich knowledge of traditional herbal plants and medicinal animals [28, 36, 37]. Ecological knowledge of herders seems to be fairly independent of the scientific botanical or ecological knowledge though knowledge has been significantly affected by schooling and recently by the Internet and social media . For the moment, we are not aware of any detailed documentation of the folk habitats Mongolians recognize, name, and use in their everyday activities or any traditional landscape partitioning of a concrete Mongolian landscape.
Traditional habitat knowledge has been documented in an increasing number of cases in temperate and boreal regions of the Northern Hemisphere, for example, among the Gitskan and Kaska First Nations in Canada [39, 40], among the Alleutais in the French Alps [13, 41], among herders in the Hortobágy forest steppe in Hungary [16, 20], Sami herders in Scandinavia , and among the Csángós living in the Carpathian Mountains in Central Europe [22, 42]. Comparison of these classifications and partitionings may help us better understand how people perceive landscapes. However, comparing folk habitat classifications seems to be more difficult than comparing plant folk classifications, as habitat knowledge is more implicit and more variable, and often more difficult to elicit [20, 43, 44], and we also lack a globally standardized habitat taxonomy.
In this paper, our objectives are to reconstruct the folk habitats and the partitioning of the landscape into these folk habitats by Mongolian herders in a forest steppe area in Northern Mongolia and to compare it with other Northern Hemisphere boreal-temperate (and some tropical) classifications.
Materials and methods
The study area is located in Seruun Gilad, in Arbulag soum (district) at the border to Bayanzurkh soum, in Khubsugul province, Northern Mongolia (coordinates N 50° 22′ 47.8″, E 99° 31′ 52.1″) (Fig. 1). The area lies 1300–1900 m above sea level and has a diverse geomorphology with steep slopes and gentle hills, rock outcrops, and river floodplains. The area belongs to the mountain forest steppe of the Khangai region [45, 46], with relatively natural vegetation utilized by relatively traditional pastoralist communities. According to local herders, the area is a cold upland pasture area with patches of forest. It lies in the permafrost region of Mongolia. The climate is characterized by 250–450 mm annual precipitation; the average monthly temperatures range from + 12 °C in July to − 21 °C in January. The mean yearly temperature is − 4.5 °C, the absolute maximum is + 35 °C, and the absolute minimum is − 49 °C .
Land use is based on semi-nomadic livestock keeping. Summer campsites are set up along streams or on lower hills close to the streams. Various types of livestock including sheep, goats, yaks, cattle, and horses are the main source of living. There were 347,159 heads of livestock (184,545 sheep, 130,000 goats, 13,984 horses, and in total 18,421 cattle and yaks) in Arbulag soum in 2017 (which has 320,550 ha of pasture, and its total area is 352,921 ha . In recent years, there has been an increased impact of livestock grazing and climate change in this area, affecting rangeland conditions, e.g., species composition, vegetation structure, and productivity . General degradation of rangelands is present in the study area as well. Overgrazing and its consequences are related to the free-moving right of Mongolian herders and to the overcrowded livestock [35, 50].
Most families use the study area for summer pasturing, except one family who also has the winter pasture in the northern part of the area.
Ethnic groups living in the study area (in Arbulag and Bayanzurkh soums) are mainly Khotgoid, Darkhad, and Khalkh communities. These communities are mainly pastoralists; the Darkhad community is well-known and studied because of Shamanism . Locals still possess a relatively traditional culture and a characteristic semi-nomadic lifestyle and customs, with rich folklore and religious life.
In 2017, we prepared a detailed vegetation (habitat) map of the study area based on the scientific (botanical) understanding of the vegetation but also taking herders’ perceptions into consideration when developing the habitat classification for the mapping (Fig. 2). A Bing map satellite image and QGIS 3.4.3. software were used. During mapping, all vascular plant species found were identified and listed; 179 species were collected and deposited in the herbarium of the Institute of General and Experimental Biology of the Mongolian Academy of Sciences, Ulaanbaatar.
The vegetation of the study area is mainly composed of mountain forest steppe, dominated by larch forests (dominant species: Larix sibirica Ledeb., Vicia amoena Fisch., Trollius asiaticus L., Poa nemoralis L., Trisetum sibiricum Rupr., Polemonium chinense (Brand) Brand, Valeriana officinalis L.), mountain meadow steppes (dominant species: Festuca lenensis Drob., Echinops latifolius Tausch, Gentiana decumbens L.fill., Schizonepeta multifida (L.) Briq.) and wet habitats (dominant species: Carex duriuscula C.A.Mey., Primula nutans Georgi, Bistorta vivipara (L.) S.F.Gray, Parnassia palustris L., Juncus triglumis L., Gentiana pseudoaquatica Kusn.) (Table 1).
Larch forests have a sparse shrub layer, even the non-grazed ones. In the inner—non-grazed—parts of the forests, forest-interior species dominate, typical species of pastures are scarce, the moss layer is deep and dense, and there are a large number of dead trees lying on the ground (standing dead trees are unexpectedly rare). Stumps (indicating wood harvesting) and livestock dung (indicating grazing) are rare (or there is none) in these deeper forest areas. Small forest patches have almost no forest-interior flora, and the ground is dominated by shade-tolerant grassland species or is bare (with larch leaf litter, the whole patch can be regarded as a forest fringe). Forest fringes are usually not sharp, but 20–100 m wide, without a sudden shrubby edge. Larch canopy opens up gradually either without any or with a Salix-dominated shrub layer. Forest grazing impacts the outer 40–100-m-wide belt of the bigger forest patches while smaller forests are grazed through totally.
Grasslands are meadow steppes. Ungrazed stands are rich in tall herbs and bushes. However, as most of the grasslands of the study area are moderately or heavily grazed, grass height is low (< 10–20 cm). Grasslands have a closed grass layer, which only opens up on dry, sunny, and rocky slopes. Pebble banks (sayr) are often sparsely covered with vegetation (< 20%). In spite of being flooded periodically, pebble banks are dry most of the time. Wet grasslands only occur along water courses; wetter types are tussocky. There is no marsh vegetation in the study area, but there is a bigger river to the west and a salt lake to the east. Limestone outcrops facing south have a sparse vegetation while rock vegetation on north-facing slopes and surrounded by forest is shaded and moist.
Data collection and analysis
Data collection on traditional ecological knowledge related to folk habitats was based on indoor and outdoor face-to-face interviews, interviews during landscape walks, and participatory fieldwork.
The study was conducted from 2016 to 2018 by a team of orientalists, botanists, and ethnoecologists. The orientalist/Mongolist of the research group is an expert of Mongolian studies including the ethnozoological knowledge of Mongolian herders . He provided cultural insights for the other Hungarian members of the research team that helped reduce or avoid misinterpretations of the data.
In July–August 2016, we visited the area and contacted the families who would be available and willing for our research project in the longer run. Prior, inform consent was asked for following the guidelines of the International Society of Ethnobiology (ISE, 2006). The preliminary list of plant species and habitats recognized and named by locals in the Seruun Gilad area was prepared by conducting structured interviews using colored photos regarding the local flora of the region . Furthermore, photos were taken to show the salient and/or common local plant species and characteristic landscape elements (potential folk habitats).
In June 2017, we visited the same herder families as in 2016. Thirty-nine to 41 pictures of local wild plant species were shown asking them—in a semi-structured way—to name the species and explain the general features and habitat preferences of these species. Additionally, 25+ pictures depicting local habitats were shown to our interviewees in order to elicit local habitat names and the partitioning of the local landscape into folk habitats. During landscape walks, we visited with herders all parts of the study area and we collected additional data on recognized and named plant species and habitat types and made additional documentary pictures for use in future interviews. Additionally, we used 40 plant species pictures for a pile sort exercise and also asked herders to free list main pasture types.
In July 2018, we conducted structured interviews. We asked the locals about the habitat preference of altogether 76 salient local wild plant species. We were able to collect more than 8 independent datasets regarding all the 76 plant species (8 families, i.e., ca. 75% of the families living in the valley). For the habitat preference of a further 64 species, we asked a knowledgeable and experienced herder. Data were collected indoor, but we made outdoor (walking) interviews and participatory fieldwork as well.
Altogether, we interviewed 20 people (15 male and 5 female) from 11 families, 18 of them were full-time herders. The number of informants was limited as landscapes further away from the research site were ecologically different. Interviewees were between 30 and 70 (average 45) years old. Interviews were conducted in Mongolian by GB and ÁA. Interviews ranged from 15 to 118 min. All interviews were digitally recorded (usually both by voice recorder and camera).
First, we transcribed all relevant parts from the interviews. Then, we merged all habitat preference data for each plant species, then grouped all habitat data into main habitat types (defined by the authors, so they do not necessarily reflect local understandings) and described their scientific meaning in English and also provided literal translations. Later, habitats were classified into macro-, meso-, and micro-scale habitats (cf. ). Macrohabitats occupy usually large areas and comprise many habitat types (a mosaic), mesohabitats are usually smaller in extension and homogenous and are often dominated by one vegetation type, and microhabitats are embedded in mesohabitats and provide special niches for particular species. We grouped species according to the major folk habitat categories assigned by herders and also into groups of specialist, generalist, and intermediate species based on the specificity or the number of folk habitat types herders attributed the species to. We also provide some information on the most salient indicators herders used to describe and distinguish habitats. Text in italics indicates original quotations and local Mongolian folk names of species and habitats.
Folk habitat categories in the Gilad valley
Locals in the Gilad valley distinguished altogether at least 88 folk habitat categories (Figs. 3, 4, 5, 6, and 7; Tables 1, 2, 3, 4, 5, 6, 7, 8, and 9). The main categories people partitioned the landscape into were forests, wet areas/lakes/rivers/streams, rocky areas/deep valleys, and dry “normal” pastures in valleys, flat areas, and gentle slopes. The most often mentioned habitat types were as follows: uuliin enger, öwör (mountain south slope), uuliin bel (foothill), oi dotor, modon dotor (in the forest), sudag, sudgiin zah (shallow coomb), buudal gazar (nomad campsite), oin zah (forest fringe), oin tsol tsoorhoi, oin chölöö (forest opening), had asgan dund (between rocks), goliin zah (riverside), tal höndii (valley), öwöljöönii gazar (winter place), chiigleg gazar (dampy area), uuliin ar, ar hayaa (north slope of a mountain), uul (mountain), uuliin zoo (wide mountain ridge), taiga (taiga), tsaram (chilly strip on the northern side close to the ridge), hadarhag gazar (rocky place), and jalga (coomb).
Below, we list and describe all folk habitats grouped into the following main categories: macro-scale habitats, meso-scale habitats, and micro-scale habitats.
Macro-scale habitats refer to larger areas with a mosaic of several/many habitat types. Herders distinguished some main pasture complexes at the supra-local level: mountainous pastures of the Khangai region (to where the study area belongs), steppe pastures of wide flat valleys and lowlands (to the south with none or much less forest cover), taiga (densely wooded pastures to the north in the forest zone), and Gobi (desert pastures far to the south) (Table 2). In the case of some species, they referred to these far away areas when asked about habitat preference (Gobi: Allium mongolicum Turcz. ex Regel, Ulmus pumila L.; taiga: Rhododendron parvifolium Adams, Juniperus sibirica Burgsd.). They also mentioned areas where there is no permafrost and settled area (cities) as macro-habitats.
Herders partitioned the local landscape into “south” and “north” (outer) parts. South areas are closer or around the summer and winter camps and often get more manure. They said: Agi (Artemisia frigida Willd., an indicator of overgrazing) grows in south areas. In contrast, north (outer) areas are less disturbed, non-manured and less used by people (they are more wild). South areas are better for small ruminants while outer areas are better for large livestock.
Mongolians have seasonal pastures. Winter places (pastures utilized between October and May) were often mentioned as a macro-scale habitat. Winter places have some common features compared to summer (or spring and autumn) places, as they are located in less windy areas and close to warmer sunny slopes with less snow. Winter places tend to have more rugged geomorphology with deep rocky valleys. Winter campsites (the center of the winter places, with nutritious grasses) is a meso-scale habitat (see below). Herders said that the grass is keep growing (regrowing in the same season after being grazed) on summer pastures (every day the grass grows) but not on winter pastures. In winter places, the goal is to fill the stomach of the livestock, as the grass is not nutritious, because nutrients went down into the roots.
Cities (as a complex of weedy, disturbed habitats) were mentioned as a habitat for some species like Chenopodium album L. and Plantago depressa Schlecht.
In the case of some species (like Potentilla fruticosa L., Aster alpinus L., Gentiana decumbens L.fill.), herders found it difficult to assign them to specific habitats because of their widespread distribution. They said these species grow “everywhere,” which usually meant that they do not have a strong habitat preference (cf. generalist species), they can grow in many not-too-wet, not-too-rocky, and non-forested habitats. In other cases (like Achnatherum splendens (Trin.) Nevski, Allium altaicum Pall., Iris lactea Pall.), they also said “everywhere” but indicating that the species grows in most valleys and slopes in this region of Mongolia.
Forests, shrub vegetation, and forest fringes
Forests are salient habitats in this landscape. Most forests are located on the northern side of the mountains. Locals distinguished 13 forest types based on the structure (density), age, and health status of the forest (Table 3). They also distinguished coniferous forests (shilmüüst mod, referring to Larix leaf) from leafy forests (navchit mod, leaved trees). However, the latter category did not occur in the study area. Herders also distinguished hard trees (Larix sibirica Ledeb., Betula sp., Populus spp.) and soft trees (Pinus sibirica Du Tour, Picea obovata Ledeb.). Soft trees do not grow alone, they always form large patches—herders said.
The area of forests usually does not increase under this cold continental climate. Some herders said that present forest patches came to exist when the world was created, similarly to rocks. Forests were scattered in the landscape at that time, and this is what we have now. Herders argued that the spatial pattern of forest patches has been stable on longer term (centuries). The average diameter of trees does change (grow), but the place of the forest would never change, not even after an earthquake—they said. Tree growth is very slow in this area, trees live long, and herders separated forests that have a good future (renewable forest) or bad future (dying forest). Herders said that some forests have a rejuvenating ability (if you cut the trees, they will regrow); in other cases, the forest is “dead” (i.e., will not regenerate if cut because there are no young trees among the old ones). The small forest patches were called orphan forests (önchin zuraa, zuraa mod) and protected from extensive wood cutting. Forests are open and sparse in windy places.
Locals do not usually cut trees near the forest edge and in small forests neither trees with specific characteristic shape, because they argue the cutter would be threatened by a lightning strike or be injured. They cut their firewood (only dead wood) from the forest interior in autumn. They argued: Everything in nature revives/regrows when spring starts, and becomes sleepy when autumn starts. Everything is connected in nature. Therefore we cut our firewood in autumn.
Pastures in or near the forest are important for livestock. Herders distinguished four pasture types in the forest: (1) patch with willow, (2) borog (Carex spp.) along the stream or water, (3) leafy plants, and (4) hyag (Agropyron cristatum (L.) Beauv.). In droughts, herders will drive their livestock into the forest and some areas close to the forest, because there is water there (the area is dampy, they said, roots of trees keep a lot of water, ca. 300 litres water per tree). In the winter, forests are warm and they are fine for the livestock. They added that in severe and heavy rain, they will graze their livestock in the forest. The forest grasses are fresh. Herders argued that pastures among the trees are worse (are of lower nutritional quality) than the pastures on dry mountain slopes. Sheep sometimes goes (without the supervision of the herder) deep into the forest (further in than the forest fringe zone) to graze on darsh (Vicia amoena Fisch.). Herders said: the deep forest is dangerous for the livestock because of carnivores and I drive the sheep out from the forest before sunset because of wolves. Horses may go even deeper into some forests as they are free ranging. Livestock grazes less in the forest in summer and more in autumn. Herders added that it is good to have the noon rest in the forest. They also added that if there is snow before the grass dies, and it remains green during the fall, grass in the forest will stay green and keeps under the snow until spring. It means that nature is making a plant silage itself. This green grass is beneficial for the livestock.
There are only few shrub-dominated places in the study area, willows (Salix pseudopentandra (B.Flod.) B.Flod., S. divaricata Pall.) being the most common shrub species. Willows grow along forest fringes and in wet meadows (red willow (Salix turanica Nas.) grows in borog place, see below). Willow shrub is a key pasture habitat in spring and summer, herders said: willow has a bitter taste (=good), I drive them into the willow shrub in the morning. Willow shrub is a natural oasis, it is a crucial pasture in droughts, it is good against parasites. Grasses growing among willows are “hotter grasses” (see below), they are greener, because the habitat is more dampy and shady. Most shrub species are grazed by the livestock; thus, they can often only survive among rocks out of reach of animals.
Herders distinguished four forest fringe types: (1) with willow, (2) with pea shrub (Caragana jubata (Pall.) Poir.), (3) with hyag (Agropyron cristatum (L.) Beauv.), and (4) with rocks. Most forest fringes are important pastures, especially those on the backside (northern slopes). Forest fringes turn yellow later, only in late autumn. These habitats are full of hyag and leafy species (like Bromopsis pumpelliana (Scribn.) Holub., Agropyron cristatum (L.) Beauv., Bistorta alopecuroides (Turcz. ex Meissn.) Kom). Herders said: leafy plants, hot plants (like dagsh: Oxytropis pseudoglandulosa Gontsch. ex Grub.) grow close to the forests, it is a good pasture, sheep has a good time there.
Dry and mesic grasslands
There are many different types of grasslands in the Gilad area according to herders, for example, the grasslands on sunny slopes, foothills, plains, on the northern sides, in forest openings and along forest fringes, on rocks, and in the hay fields of the winter places (Table 4). Grass is the green gold—herders argued.
Herders said that grass is denser and taller on the northern slopes because the site is more shady and has a better water supply. The grass is more palatable but less nutritious, and the animals are cold there in the winter. These slopes have a lot of borog (here Carex pediformis C.A.Mey., Poa pratensis L., Kobresia spp.) – herders said. The uppermost part of the northern slopes is a cool windy habitat with some specialist species (this plant (Dryas oxyodonta Juz.) does not grow at lower elevation). The grass is thin and (structurally) fine, livestock likes to be there.
Southern slopes are sunny, grass is less dense, sparse, and always drying out, but of higher forage quality. All herders agreed on these. The soil on the southern slope is relatively dry and dries up quickly. Roots of the plants are sparse; the land is often grassless. Sheep and goats graze a lot there in spring because the roots of the plants unfreeze early in the spring. Sheep and goats (also called thin animals, nariin mal) like grazing on southern places. They also added that on dry mountain, slopes there is no hyag (Agropyron cristatum (L.) Beauv.), leafy plants, and sharilj (Artemisia macrocephala Jacq. ex Bess. and some other ruderal Artemisia species). Herders said that they must graze animals in these inner pastures, especially early morning, in cool spring and autumn and in cold winter (you have to start the grazing route here in the morning, livestock will give a lot of milk, it will fatten well). They said what Mongolians often recall that: You do not feel cold, if you follow the sun, and you do not feel hungry if you follow the animals.
In free listings of pasture types, herders usually answered with a list of dominant folk taxa: botyuul (Festuca lenensis Drob.), borog (Carex duriuscula C.A.Mey. and other species), hyag (Agropyron cristatum (L.) Beauv.), ders (Achnatherum splendens (Trin.) Nevski), shivee (Stipa spp.), sharilj (Artemisia tanacetifolia L., and other species), and luul (Chenopodium spp.). In other cases when we asked about the main grassland types, they listed (1) shireg (grasslands near the stream, in valleys, (2) botyuul (Festuca lenensis Drob. on the slopes), (3) leafy-hot grasses (around forests on the slopes, with hyag and botyuul), and (4) hyag at winter campsites.
Herders always argued that botyuul is very good for the livestock, animals like eating it, and fatten quickly on it, adding that botyuul is the best grass what livestock can find to graze upon in Mongolia. When 40 plant species were pile-sorted by a herder, after 40 min of sorting species into trees, flowering plants, leafy plants, hot plants, summer forages etc., he lifted the picture of botyuul, and said: and this is THE botyuul!—which did not belong to any of the piled groups. Herders listed four types of botyuul: gold, red, white (or thick), and yanzagan (fawn). They also said that botyuul dominates in three pasture types: botyuul with borog (where we found Festuca lenensis Drob., Carex sp., Agrostis trinii Turcz., Koeleria cristata (L.) Pers.), botyuul with hyag (with Festuca lenensis Drob., Agropyron cristatum (L.) Beauv., Poa palustris L., Bromopsis pumpelliana (Scribn.) Holub.), and pure botyuul (Festuca lenensis Drob.). Borog is a complex term. Borog includes Kobresia spp. and Carex duriuscula C.A.Mey. and other similar Monocotyledons (i.e., short and dry grasses growing on gently sunny slopes and plain areas), but the word borog was also used for dried shireg (dried wet meadows, see below).
There are only few habitat types where herders make hay for the winter (and they make only a little compared to the size of the herds). The most important hay meadows are in or near the winter campsites (but also in forest openings and in some drier valleys). Hay meadows are often fenced from livestock, are mown in August, and are dominated by hyag (Agropyron cristatum (L.) Beauv.). Hyag is a hot grass (meaning nutritious). Hyag has no flower—herders argued—but it has a head. It grows at winter places, in forest fringes and in shireg.
Though the area has a continental forest steppe climate, there are many places in the landscape where water comes near or flows on the surface and accumulates in lakes and thus gives rise for specific habitat types, for example, shireg, “along streams,” lake, spring, tussocky area, borog place, riverside, damp area, marshland, or “bend of the river with Iris lactea Pall.” (Table 5).
Shireg (green meadow) is one of the most important of these. It is a lawn, a dense sward, which is very damp, and the bare soil can not be seen. Its dominant species is Carex duriuscula C.A.Mey. (N.B. the official Mongolian name of C. duriuscula is shireg ulalj). However, locally, shireg has two names: shireg when it is growing (green grass—zuleg) and borog after it has dried. Herders argued that in shireg animals do not fatten, they fatten on dry slopes with botyuul. Cattle grazes in borog in winter. Greener meadows in a small flat valley are referred to as borog shireg or borog sudag. Borog shireg (with Festuca lenensis Drob., Carex duriuscula C.A.Mey., Gentiana squarrosa Ledeb., Bistorta vivipara (L.) S.F.Gray) is found on slopes close to shireg-dominated valleys, while borog sudag is found along shallow coombs on hillsides (Festuca lenensis Drob., Carex pediformis C.A.Mey., Poa sp., Kobresia spp.).
A salient habitat is the tussocky grassland dominated by Carex duriuscula C.A.Mey., Bistorta vivipara (L.) S.F.Gray, Cirsium esculentum (Siev.) C.A.Mey., and Primula farinosa L. Herders argued that tussocks grow in height (they are higher than the surrounding surfaces). They grow where there is water. Nature created them, ice, water and drought. The top of the tussocks is an important first pasture in spring when the sun melts the snow. They also observed that the heads of the tussocks have turned black recently and they argued that this is because underground water is decreasing.
A specific habitat is found around springs with salty water. Similar salty habitats are found around bigger lakes (towards Murun). Here, the salt grows out from ground.
Rocky, barren habitats
Eight rock habitat types were distinguished by herders based on the size of the stones and rocks, pattern and mobility of these and the vegetation between them, and the location of the habitat in the landscape (close to rivers or surrounded by forests) (Table 6).
They argued that sparsely vegetated rocky slopes are better quality pastures than the dense shireg areas along streams. Rock grasslands are often grazed intensively at winter pasture places. Overgrazing loosens the soil surface and causes erosion—herders said. Goats especially like grazing on rocky and stony places.
They also separated habitats with stones that are fixed in the ground (like mountain rocky slope, screes in the forest) and stony habitats that have stones lying on the surface (and thus can be moved away easily) (mountain stony slope). One herder listed four types of rocky habitats: (1) place with tsahir rock (blue soil) with less-palatable (borog) grass, a site inappropriate for livestock grazing; (2) place with white stones, black rocks, or red rocks, where palatable grasses grow and thus are good for livestock grazing; (3) place with brown rock with Salix spp., Cotoneaster melanocarpus Fisch. ex Blytt., Urtica angustifolia Fisch. ex Hornem.; and (4) place with bad soil, loosened soil, and red sand, such places can easily be degraded by livestock.
Local rivers are fast flowing and often have floods. Herders distinguished habitats with a high density of stones: sayr has pebbles while dairga has unrounded stones and is difficult to cross. Both have small vegetation cover.
Screes are formed on steeper slopes and may provide refuges for less grazing-tolerant species. Some screes are surrounded by forest and have a damp microclimate. Herders distinguished these habitats as they provide important wild fruits (e.g., Ribes altissimum Turcz. ex Pojark., Rosa acicularis Lindl.).
Areas intensively used by humans and livestock were regarded as degraded. These habitas have short grass or are totally bare, grassless. Nomad campsites have a diverse set of disturbed, weedy habitats: animal pens, dung covered areas, weedy areas with sharilj, and strips along fences (Table 7). Herders said that rubbish grasses (weeds) like sharilj and luul (Chenopodium spp.) grow on these ruderal (rubbish/debris), overfed places, where the soil is erroneous. They said that these places provide the first-grown forage in spring. Herders said that on denser pastures, the roots of pasture plants rule the earth; thus, sharilj can not grow there, it has no chance at all, the vegetation is saturated, so there are no pasture weeds on the pastures further from the summer and winter campsites.
Herders used the expression lifeless soil (ühmel hörs) for areas near the yurt at nomad camps sites or on abandoned yurt and pen places where the soil is “soiling back.”
Geomorphologically defined habitats: slopes and valleys
Herders often referred to geomorphological features when describing habitats of wild plant species: for example, on the southern or northern slopes, on foothills, or on flatter or sharper ridges (Table 8). They argued that valleys have wetter soil because there is more snow there which melts later. Often, geomorphology-based names were combined with other meso-habitat names (e.g., shallow coomb on the mountain northern side, foothill with rock and loose soil).
Micro-scale habitats are usually formed at a finer spatial scale than meso-scale habitats. However, the separation is not sharp. Typical microhabitats were the marmot burrows that had disturbed vegetation with species with higher nutrient needs (cf. the manuring effect of marmots and the effect of the loosened soil) (Table 9). Borog is growing “on the top of the tussocks,” while Atragene sibirica L. “creeps on the tree.” Mossy forest floors are distinguished as a habitat for Ledum palustre L., Vaccinium spp., Rhododendron parvifolium Adams, and Juniperus pseudosabina Fisch. et Mey., while weeds accummulate around manure and trash heaps, along fences and roadsides.
Key dimensions of the local landscape partitioning
Herders distinguished habitats using diverse features. These features could be grouped into some major dimensions (sensu [19, 22]), like geomorphological features (e.g., slope, ridge, coomb), hydrological features (river, lake, wet meadow, marshland), edaphic (bedrock, soil) features (rocks, screes, sayr), topography (lowland steppes, high mountain treeless areas), human and animal disturbance (lifeless earth, nomad campsites, marmot burrows), dominant plant species (Larix forest, botyuul-dominated grasslands, shireg, borog, mossy forest floor), vegetation structure and physiognomy (forest edge, sparse forest, tussock grassland), land use (pastures, hay meadow), and succession (young forest, regenerating grassland).
Salient plant species of the local landscape partitioning
Habitat of one species is given by mentioning another species
In several cases, herders defined the habitat of a species by refering to another species that often co-occurs with that—usually habitat specialist—species (Table 10). Salix spp. (mostly S. turanica Nas.), Larix sibirica Ledeb., and borog (small growing Carex spp.) were most often used for this purpose.
Habitat specialist and habitat generalist species
We collected habitat preference data for 76 wild plant species (Table 11). Some species occured almost everywhere, and some others had a single specific habitat. Herders often came up with their answers iteratively as many species occured in several habitat types. Typical generalist species in this landscape were according to herders, for example, Potentilla fruticosa L., Pulsatilla turczaninovii Kryl. et Serg., Rhododendron parvifolium Adams, Allium altaicum Pall., Rheum undulatum L., and Artemisia macrocephala Jacq. ex Bess., while habitat specialists were, for example, Papaver nudicaule L., Aconitum barbatum Pers, Atragene sibirica L., Glaux maritima L., Primula farinosa L., and Leptopyrum fumarioides (L.) Reichenb.
Other salient species groups
There were some species and species groups that were often used to describe habitat types (see above: botyuul, hyag, shireg, borog). Most of these had high (or low) forage quality. Herders know these species for example by tasting them. One herder said: a good herder tastes all the grasses on his pasture.
There were two species groups locals also often mentioned: hot and cold grasses and leafy plants.
Hot grasses are leafy, they are of high quality, and they stay in the livestock, while cold grasses only fill the stomack, and go through the livestock (without much effect on meat or milk production). They argued that livestock should eat hot grasses in the summer to fatten well. Hot grasses are, for example, Artemisia frigida Willd., Oxytropis pseudoglandulosa Gontsch. ex Grub., Pedicularis spp., Agropyron cristatum (L.) Beauv., Pulsatilla turczaninovii Kryl.et Serg., Pulsatilla flavescens (Zucc.) Juz., and Echinops latifolius Tausch.
Leafy plants have large leaves, and their most salient feature is that they are trampled and destroyed by livestock easily in autumn, while grasses are less impacted. Examples are Gentiana macrophylla Pall., Plantago depressa Schlecht., Vicia amoena Fisch., Pedicularis resupinata L., Valeriana officinalis L., Aegopodium alpestre Ledeb., Sanguisorba officinalis L., Hedysarum alpinum L., Rumex acetosa L., and Trollius asiaticus L. They have various nutritional value.
Mongolian herders had a deep knowledge of the habitats of their landscape and of the habitat preferences of the 76 plant species interviewed. They distinguished altogether at least 88 folk habitats. Folk habitat categories were more or less discrete units, perceptually and functionally distinct elements, but often had diffuse boundaries towards neighboring types (cf. [21, 22]). Geomorphologically defined habitats had the highest number of categories, followed by forests, wetland, and rock habitats.
Naming of folk habitats
Many folk habitat names were shorter or longer descriptive expressions often using common words (e.g., wet meadow with tussocks along stream; dampy shallow coomb on the nortern slopes with bushy pea shrub and willow; flint rocky place with sand and low grass). This might indicate flexibility (cf. ) and the lack of a fixed terminology for many habitat types listed in Tables 2, 3, 4, 5, 6, 7, 8, and 9. In other cases, habitats had a short and specific name (e.g., taiga, Gobi, tsaram, shireg, borog), and people understood the same under these names. Hunn and Meilleur  suggest that these habitats and names provide the basic level of the local landscape partitioning—landscape elements which are particularly salient to the local community. Molnár [16, 20, 52] reports that a large number of synonyms are attributable to the erosion of knowledge, limited knowledge sharing, and diverse ethnic origins of locals. In contrast, in other landscape partitionings [14, 22, 53, 54], categories are highly lexicalized and have only few synonyms.
Several habitat terms were locative, especially in the geomorphological and hydrological sets (e.g., among the trees), and were literally the same as those used by the Csángós in the Carpathians , by the Matsigenka in Amazonia , and by the Gitksan and Kaska in Canada [39, 40].
Habitat names did not reflect directly the usefulness of the habitat (e.g., forage quality), but during the interviews, locals often described the nutritional quality and palatability of the vegetation in the various habitats. The livelihood of the local community had an impact not only on the knowledge of various plants species, but on the local knowledge of habitats as well, they usually described habitats through the eye of their livestock (cf. [12, 42, 52, 55]).
Scale of folk habitats
Herders distinguished macro-, meso-, and micro-scale habitats (sensu ). One reason for the use of different spatial scales may be ecological, since plant species occupy somewhat different niches in a landscape: some species are specialist, while others are generalist—occurring in various habitats in the landscape. For a precise description of species-specific habitat preferences, a multi-scaled landscape partitioning might be better suited (cf. ). We also found, just as previous studies had observed [14, 20, 22, 44, 56] that abiotic features (e.g., geomorphology, hydrology, edaphic conditions) often defined larger, broader habitat categories, while biotic features defined habitats were used in the finer-scale partitioning.
Most habitats (77%) belonged to the meso-scale, while macro-scale and micro-scale habitats were few; however, research methodology (less participatory field work) might be partly responsible for this.
Herders’ perceptions of spatial variability in their environment are reflected in their nomadic herding strategy . A key division of the landscape is by partitioning it into winter and summer places (pastures). Summer places—where the main goal is fattening and rearing youngs—are chosen by ecological criteria including availability of water for livestock and domestic use and availability of optimal forage types for the different kinds of livestock (cf. [3, 50]), while winter places serve to keep the condition of the livestock as far as possible till the spring and are chosen based on available forage and wind and snow conditions.
Herders distinguished two major parts in the summer place: inner and behind (outer) parts, former one being closer to the valley bottoms and yurts (for a similar partitioning, see ). However, we could not find a sharp distinction between primary (hardly human-transformed) habitats and semi-natural/agricultural habitats which is a well-documented basic dichotomy of the folk habitat classification systems of several tropical peoples (e.g., primary forest vs. secondary forest in swidden systems) [14, 44, 53]. In our study area, cultivated lands and other drastically transformed habitats are totally missing. The main reason for this is probably rooted in the traditional beliefs of Mongols (and most of Inner-Asian nomads); human beings have no right to change anything in their surrounding, any change should happen spontaneously, naturally.
Dimensions of the Mongolian landscape partitioning
Mongolian habitat categories were not organized into a single hierarchy; the partitioning was multidimensional. The multidimensional description of habitats incorporated several sets of features and made the nuanced characterization of plant species’ habitat preferences possible.
Based on our understanding, exposure of slopes and valleys in between gave the major structure to the classification. Otherwise, Mongolians distinguished habitats by the following features (Tables 3, 4, 5, 6, 7, 8, 9, and 12): geomorphology, dominant plant species, soil and bedrock types, hydrological features, topographic features, vegetation structure, successional stage, land use, and disturbances. Fernández-Giménez  also found that Mongolian herders classify pasture habitats using a diverse set of criteria, including nutritional quality, topography and elevation, aspect, ecological zone and plant community, color, soil characteristics, water quality and quantity, distance from camp, and degree of utilization by livestock.
In other parts of the world but in similar mountainous environments like in the Carpathians  and the Alps [13, 41, 57], locals use similar features in the recognition and naming of habitats to partition their landscapes (Table 12). Johnson [39, 40] also documented the importance of physiography, hydrologic features, vegetation, and also wildlife habitats among Gitksan and Kaska Dena First Nations in Western Canada. In the European mountainous landscapes, especially in the Carpathians, land use seems to be the key dimension, while all other habitat categories are actually refining the basic land-use types—forests, haymeadows, pastures, and arable fields [13, 22, 42].
On the contrary, in geomorphologically more simple landscapes, habitats can be defined by various abiotic and biotic factors that are arranged along a key gradient (very gently slope with changing soil quality, i.e., dimensions highly correlate), while many possible gradients (e.g., woody/non-woody, mountain/valley, rock/sand, naturalness) can be missing [Hortobágy: 20, 52; Amazonia: 56].
Vegetation (and vegetation-dominated habitats) can be classified in many ways. Methodologies are based on species composition (see, e.g., the most commonly used scientific so-called Braun-Blanquet phytosociological approach ), vegetation physiognomy, vegetation structure, or environmental factors. Mongolian herders never used species composition (list of characteristic and dominant plant species) as one of their features, similarly to Csángó people and Hortobágy herders [20, 22]. Mongolians used edaphic, hydrological, vegetation, structural, etc. features instead.
In summary, local landscape partitionings differed considerably in the importance of various dimensions used, with edaphic, geomorphological, hydrological, and dominant species-based dimensions having higher, while topographical, successional, and zoological dimensions having lower importance.
Geomorphologically defined habitats (like slopes, ridges, valleys) were common in our study area. Reasons behind this high number might be that (1) the landscape has a diverse geomorphology, (2) the different habitat types have very different usability (e.g., forage value), and (3) geomorphological features play an important role in orientation (e.g., routes for long-distance travels).
Aspect (exposure) was a crucial feature. Southern and northern slopes were sharply distinguished. In the Northern Mongolian forest steppe area, forests almost exclusively occur on northern slopes, while southern slopes dominated by meadow steppes  provide high-quality forage for the livestock (cf. hilly and mountainous temperate landscapes in the northern hemisphere [22, 39]).
Dynamic aspects, like changes in vegetation and other habitat features, were also mentioned several times. Forest changes are slow in this region partly because of very slow tree growth rate, partly because forest edge trees are protected both by local customs and the state from cutting . The habitats “young forest,” “old forest,” and “dying forest” indicated the understanding and importance of forest regeneration and succession, but forest use was less intensive, and so, the sequence was much less detailed than in the Carpathians . Shrub habitats were few, probably because most shrub species are grazing intolerant and are rare. Screes serve as refuges for several shrub species and herders often assigned shrub species to these habitats.
Herders were aware that grassland dynamics is slow partly because of the dense root system (the roots of pasture plants rule the earth, the vegetation is saturated). The fastest grassland succession was observed by herders on places on recently abandoned yurt and pen sites that were also called lifeless soil (documented as “death of the soil” by Fernández-Giménez ).
Mongolians like to exist in the landscape in a way causing as little disturbance as possible. This may be one of the reasons why heavily disturbed places occupy small areas; vegetation stands with fast successional dynamics are less common than in other landscapes in the temperate region. Csángó people in the Carpathians also do their best to minimize disturbance and/or facilitate regeneration as effectively as possible during farming (though farming implies a complex set of deliberate and undeliberate disturbances) because disturbances may reduce the amount and/or quality of hay biomass, which they try to avoid. This might be a reason why disturbance is a salient feature in their landscape partitioning .
Herders often mentioned salient plant species and morphologically or ecologically salient indicator species when describing habitat types or habitat preference of other species (see also [24, 56, 60]). Most specialist and generalist species regarded as such by local herders were regarded so by us as well. Local and scientific understandings seemed to correlate. The majority of indicator species were woody in our study area [similarly to [54, 56], but see , with primarily herbaceous plants].
A good Mongolian herder is said to constantly monitor both his herds and his pastures, seeking to “harmonize” the needs of his stock with temporal changes in plants, weather, and water availability . Our informants had the same view and explained to us that the herder does not follow the livestock (passively), it is his duty to think (about options) and move them (to the next right place to graze or rest). They also argued that herders have to be observant, for example, tasting all important forage species of their pastures and work for the well-being of their animals. The rich traditional habitat knowledge we were able to document proves that many herders are observant and have a strong dedication to understand the landscape which provides their everyday livelihood.
We conclude that despite all the difficulties of studying landscape partitionings, conducting landscape ethnoecological research will hopefully contribute to a deeper understanding of how nature is perceived by local people at the landscape level. Folk habitat knowledge and, in general, locals’ ecological understanding seem to be a rich information source about the landscape, which can be used in resource management and nature conservation (cf. ). We hope that our study can help various stakeholders working at different governance levels and being responsible for a better management of Mongolian pasture resources, and thus, governance can better support small-scale Mongolian herders and their families. This is what—among other things—our local herder colleagues asked us to tell the world.
Availability of data and materials
Voucher specimens for species were deposited in the herbarium of the Institute of General and Experimental Biology of the Mongolian Academy of Sciences.
Berkes F. Sacred ecology: traditional ecological knowledge and resource management. New York: Routledge; 2017.
Warren A. Changing understanding of African pastoralism and the nature of environmental paradigms. Trans Inst of Brit Geographers. 1995;20:193–203. https://doi.org/10.2307/622431.
Fernández-Giménez ME. The role of Mongolian nomadic pastoralists’ ecological knowledge in rangeland management. Ecol Appl. 2000;10:1318–26.
Barani H. Teaching the shepherds or learning from them?: the Iranian experience. Anthropol Notebooks. 2007;13(1):69–73.
Chantsallkham J, Reid RS, Fernández-Giménez ME, Tsevlee A, Yadamsuren B, Heiner M. Applying a dryland degradation framework for rangelands: the case of Mongolia. Ecol Appl. 2018;28(3):622–42 https://doi.org/10.1002/eap.1684.
Volpato G, Puri RK. Dormancy and revitalization: the fate of ethnobotanical knowledge of camel forage among Sahrawi nomads and refugees of Western Sahara. Ethnobotany Research and Applications. 2014;12:183–210. https://doi.org/10.17348/era.12.0.183-210.
Roturier S, Roué M. Of forest, snow and lichen: Sámi reindeer herders’ knowledge of winter pastures in northern Sweden. Forest Ecol and Manag. 2009;258:960–7 https://doi.org/10.1016/j.foreco.2009.07.045.
Roba HG, Oba G. Efficacy of integrating herder knowledge and ecological methods for monitoring rangeland degradation in Northern Kenya. Hum Ecol. 2009;37:589–612 https://doi.org/10.1007/s10745-009-9271-0.
Molnár Zs. Perception and management of spatio-temporal pasture heterogeneity by Hungarian herders. Rangeland Ecol Manag. 2014;67:107–18 https://doi.org/10.2111/REM-D-13-00082.1.
Galvin K. Transitions: pastoralists living with change. Annu Rev Anthropol. 2009;38:185–98 https://doi.org/10.1146/annurev-anthro-091908-164442.
Hunn E. Ethnobiology in four phases. J Ethnobiol, 2007;27(1):1–10. https://doi.org/10.2993/0278-0771(2007)27[1:EIFP]2.0.CO;2.
Berlin B. Ethnobiological classification. Principles of categorisation of plants and animals in traditional societies. Princeton: Princeton University Press; 1992.
Meilleur B. Alluetain ethnoecology and traditional economy: the procurement and production of plant resources in the Northern French Alps, PhD thesis. Washington: University of Washington; 1986.
Shepard G, Yu DW, Lizarralde M, Italiano M. Rain forest habitat classification among the Matsigenka of the Peruvian Amazon. J Ethnobiol. 2001;21:1–38 https://ethnobiology.org/sites/default/files/pdfs/JoE/21-1/Shepard-etal.pdf.
Johnson LM. Hunn ES (eds). Landscape ethnoecology. Concepts of biotic and physical space. New York, Oxford: Berghahn Books; 2010b.
Molnár Zs. Traditional vegetation knowledge of the Hortobágy salt steppe (Hungary): a neglected source of information for vegetation science and conservation. Phytocoenologia. 2013;43:193–205 https://doi.org/10.1127/0340-269X/2013/0043-0561.
Tüxen R. Das System der nordwestdeutschen Pflanzengesellschaften. Mitteilungen der Floristische-Soziologische Arbeitsgemeinschaft. 1955;5:155–76.
Rosch E. Principles of categorization. In: Rosch E, Lloyd B, editors. Cognition and categorization. New York, Oxford: Wiley; 1978. p. 27–48.
Johnson LM, Hunn ES. Introduction. In: Johnson LM, Hunn ES, editors. Landscape ethnoecology. Concepts of biotic and physical space. New York, Oxford: Berghahn Books; 2010a. p. 1–11.
Molnár Zs. Classification of pasture habitats by Hungarian herders in a steppe landscape (Hungary). J Ethnobiol Ethnomed. 2012a;8:28. https://doi.org/10.1186/1746-4269-8-28.
Hunn ES, Meilleur BA. Toward a theory of landscape ethnoecological classification. In: Johnson LM, Hunn ES, editors. Landscape ethnoecology. Concepts of biotic and physical space. New York: Berghahn Books; 2010. p. 15–26.
Babai D, Molnár Zs. Multidimensionality and scale in a landscape ethnoecological partitioning of a mountainous landscape (Gyimes, Eastern Carpathians, Romania). J Ethnobiol Ethnomed. 2013;9:11 https://doi.org/10.1186/1746-4269-9-11.
Mapinduzi AL, Oba G, Weladji RB, Colman JE. Use of indigenous ecological knowledge of the Maasai pastoralists for assessing rangeland biodiversity in Tanzania. Afr J Ecol. 2003;41:329–36 https://doi.org/10.1111/j.1365-2028.2003.00479.x.
Krohmer J. Landscape perception, classification, and use among Sahelian Fulani in Burkina Faso. In: Johnson LM, Hunn ES, editors. Landscape ethnoecology. Concepts of biotic and physical space. New York, Oxford: Berghahn Books; 2010. p. 49–82.
Ouachinou JA, Dassou GH, Azihou AF, Adomou AC, Yédomonhan H. Breeders’ knowledge on cattle fodder species preference in rangelands of Benin. J Ethnobiol Ethnomed. 2018;14:66 https://doi.org/10.1186/s13002-018-0264-1.
Naah J-BSN. Investigating criteria for valuation of forage resources by local agro-pastoralists in West Africa: using quantitative ethnoecological approach. J Ethnobiol Ethnomed. 2018;14:62 https://doi.org/10.1186/s13002-018-0261-4.
Barfield T. The perilous frontier: nomadic empires and China. Cambridge: Wiley-Blackwell; 1989.
Wurchaih H, Menggenqiqig K. Medicinal wild plants used by the Mongol herdsmen in Bairin Area of Inner Mongolia and its comparative study between TMM and TCM. J Ethnobiol Ethnomed. 2019;15:32 https://doi.org/10.1186/s13002-019-0300-9.
Goulden CE, Mead J, Horwitz R, Goulden M, Nandintsetseg B, et al. Interviews of Mongolian herders and high resolution precipitation data reveal an increase in short heavy rains and thunderstorm activity in semi-arid Mongolia. Clim Chang. 2016;136:281–95. https://doi.org/10.1007/s10584-016-1614-4.
Batjargal Z. Fragile environment, vulnerable people and sensitive society. Japan: Kaihatu-Sha Co. Ltd.; 2007.
Fernández-Giménez ME, Batbuyan B, Batkhishig B. Cross-boundary and cross-level dynamics increase vulnerability to severe winter disasters (dzud) in Mongolia. Glob Environ Chang. 2012;22(4):836–51. https://doi.org/10.1016/j.gloenvcha.2012.07.001.
Damiran D. Palatability of Mongolian rangeland plants. Circular of information №3. Union: Eastern Oregon Agricultural Research Center, Oregon State University; 2005.
Soyolt, Galsannorbu, Yongping, Wunenbayar, Liu G, Khasbagan. Wild plant folk nomenclature of the Mongol herdsmen in the Arhorchin national nature reserve, Inner Mongolia, PR China. J Ethnobiol Ethnomedidne. 2013;9:30. https://doi.org/10.1186/1746-4269-9-30.
Fernández-Giménez ME. The role of ecological perception in indigenous resource management: a case study from the Mongolian forest-steppe. Nomadic Peoples. 1993;33:31–46 https://www.jstor.org/stable/43124050.
Kakinuma K, Takatsuki S. Applying local knowledge to rangeland management in northern Mongolia: do ‘narrow plants’ reflect the carrying capacity of the land? Pastoralism: Research, Policy and Practice. 2012;2(1):23. https://doi.org/10.1186/2041-7136-2-23.
Sanchir Ch. Ethnobotany: plant name meaning. Erdem of Mongolian Academy of Sciences (monthly newspaper), (in Mongolian) 2007;5(103).
Avar Á: A természet és az állatok a hagyományos mongol gondolkodásban. (Nature and animals in the traditional Mongolian worldview). Equinter, Budapest; 2012.
Éliás, BA. Mongol nomádok ma. Az akkulturáció kérdése a mobilitásvesztés okainak és hatásainak tükrében. (Mongolian nomads today. Acculturation in the light of the causes and impacts of decreasing mobility. In Hungarian.) Távol-Keleti Tanulmányok, 2017;9(1):49–61.
Johnson LM. A place that’s good. Gitksan landscape perception and ethnoecology. Hum Ecol. 2000;28(2):301–25.
Johnson LM. Kaska ethnoecology, “kinds of place,” and “cultural landscape”. In: Johnson LM, Hunn ES, editors. Landscape ethnoecology. Concepts of Biotic and physical space. New York, Oxford: Berghahn Books; 2010. p. 204–21.
Meilleur B. The structure and role of folk ecological knowledge in Les Allues, Savoie (France). In: Johnson LM, Hunn ES, editors. Landscape ethnoecology. Concepts of biotic and physical space. New York, Oxford: Berghahn Books; 2010. p. 159–74.
Babai D, Molnár Á, Molnár Zs. “Ahogy gondozza, úgy veszi hasznát” Hagyományos ökológiai tudás és gazdálkodás Gyimesben. (Traditional ecological knowledge and land use in Gyimes (Eastern Carpathians), Budapest; Vácrátót: MTA Bölcsészettudományi Kutatóközpont Néprajztudományi Intézet; MTA Ökológiai Kutatóközpont Ökológiai és Botanikai Intézet; 2014. https://www.dki.okologia.mta.hu/sites/
Ellen R. Why aren’t the Nuaulu like the Matsigenka? Knowledge and categorization of forest diversity on Seram, Eastern Indonesia. In: Johnson LM, Hunn ES, editors. Landscape ethnoecology. Concepts of biotic and physical space. New York, Oxford: Berghahn Books; 2010. p. 116–40.
Gilmore MP, Ochoa SR, Flores SR. The cultural siginicance of the habitat Maňaco taco to the Maijuna of the Peruvian Amazon. In: Johnson LM, Hunn ES, editors. Landscape ethnoecology. Concepts of biotic and physical space. New York, Oxford: Berghahn Books; 2010. p. 141–58.
Grubov VI. Key to Mongolian vascular plants with illustrations (in Russian). Leningrad: Nauk; 1982.
Gubanov IA. Conspectus of flora of Outer Mongolia (vascular plants) in Russian. Moscow: Valang; 1996.
Nandintsetseg B, Greene JS, Goulden CE. Trends in extreme daily precipitation and temperature near Lake Hövsgöl, Mongolia. Int J Climatol. 2007;27(3):341–7. https://doi.org/10.1002/joc.1404.
National statistics office of Mongolia. 2017. https://www.en.nso.mn/
Bruegger RA, Jigjsuren O, Fernández-Giménez ME. Herder observations of rangeland change in Mongolia: indicators, causes, and application to community-based management. Rangeland Ecol manag. 2014;67(2):119–31. https://doi.org/10.2111/REM-D-13-00124.1.
Fernández-Giménez ME, AIlen-Diaz BH. Vegetation change along gradients from water sources in three grazed Mongolian ecosystems. Plant Ecol. 2001;157:101–18. https://doi.org/10.1023/A:1014519206041.
Birtalan Á. The shaman (ess)–the performer: examples of the activities and life stories of Darkhad Mongolian shamanesses. I Shaman. 2007;15:69–86 https://www.academia.edu/30900364/The_Shaman_ess_the_Performer._Examples_of_the_Activities_and_Life_Stories_of_Darkhad_Mongolian_Shamanesses.
Molnár Zs. Traditional ecological knowledge of herders on the flora and vegetation of the Hortobágy. Debrecen: Hortobágy Természetvédelmi Közalapítvány; 2012b.
Martin GJ. Ecological classification among the Chinantec and Mixe of Oaxaca. Mexico Etnoecológica. 1993;1(2):14–31.
Fleck DW, Harder JD. Matses indian rainforest habitat classification and mammalian diversity in amazonian Peru. J Ethnobiol. 2000;20:1–36 https://ethnobiology.org/sites/default/files/pdfs/JoE/20-1/FleckHarder.pdf.
Molnár Z. “I see the grass through the mouths of my animals” – folk indicators of pasture plants used by traditional steppe herders. J Ethnobiol. 2017;37(3) https://doi.org/10.2993/0278-0771-37.3.522.
Abraão MB, Shepard GH, Nelson BW Jr, Baniwa JC, Andrello G, Yu DW. Baniwa vegetation classification in the white-sand Campinarana habitat of the Northwest Amazon, Brazil. In: Johnson LM, Hunn ES, editors. Landscape ethnoecology. Concepts of biotic and physical space. New York, Oxford: Berghahn Books; 2010. p. 83–115.
Netting RMcC. Balancing on an Alp. Ecological change and continuity in a Swiss mountain community. Cambridge: Cambridge University Press; 1981.
Dulamsuren C, Hauck M, Mühlenberg M. Ground vegetation in the Mongolian taiga forest-steppe ecotone does not offer evidence for the human origin of grasslands. Appl Veg Sci. 2005;8(2):149–54. https://doi.org/10.1111/j.1654-109X.2005.tb00640.x.
Gradel A, Mühlenberg M. Spatial characteristics of near-natural Mongolian forests at the southern edge of the taiga. Allgemeine Forst und Jagdzeitung. 2011;182. Jg., 3–4.
Schulz C, Martín Brañas M, Núñez Pérez C, Del Aguila Villacorta M, Laurie N, Lawson IT, Roucoux KH. Peatland and wetland ecosystems in Peruvian Amazonia: indigenous classifications and perspectives. Ecol Soc. 24(2):12 https://doi.org/10.5751/ES-10886-240212.
Babai D, Tóth A, Szentirmai I, Biró M, Máté A, Demeter L, Szépligeti M, Varga A, Molnár Á, Kun R, Molnár Z. Do conservation and agri-environmental regulations suppor effectively traditional small-scale farming in East-Central European cultural landscapes? Biodivers Conserv. 2015;24:3305–27. https://doi.org/10.1007/s10531-015-0971-z.
We gratefully acknowledge all the Mongolian herders of the Khuvsugul-Murun region who patiently and generously shared their knowledge with us: P. Jigjid, J. Erdenetsogt, N. Enkhtsetseg, Ts. Nyamkhuu, Kh. Myagmar, P. Oldokh, J. Tsetsenkhuu, Ch. Sansar, Ch. Lkhamsuren, P. Batnyam, Ts. Sarantuya, M. Bilegdemberel, S. Lhagva, Ts. Batjargal, D. Purevjav, Batkhuyag, Lkhagvasuren, Amarjargal, and Tungalag. And we thank Beata Oborny, N. Amartuvshin, and N. Saruul for their helpful comments on the earlier version of the manuscript.
GB and ZM received financial support through the project of the National Research, Development and Innovation Office (GINOP-2.3.2-15-2016-00019, “Sustainable use of ecosystem services - research for mitigating the negative effect of climate change, land use change and biological invasion”), Dániel Babai was supported by the MTA Premium Postdoctoral Scholarship of the Hungarian Academy of Sciences, as a background institution of the Hungarian Ministry of Human Capacities (EMMI). We thank Boglárka Éliás, L. Davaa, J. Laagansuren, and N. Baatarkhuu for helping in the fieldwork and Steve Kane for the language revision.
Ethics approval and consent to participate
The methods of obtaining data during fieldwork followed the guidelines set by International Society of Ethnobiology Code of Ethics and adhere to the local traditions for such research. Free prior informed consent was obtained from all study participants. No ethical committee permits were required. No permits were required to collect voucher specimens.
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Gantuya, B., Avar, Á., Babai, D. et al. “A herder’s duty is to think”: landscape partitioning and folk habitats of Mongolian herders in a mountain forest steppe (Khuvsugul-Murun region). J Ethnobiology Ethnomedicine 15, 54 (2019) doi:10.1186/s13002-019-0328-x
- Landscape partitioning
- Mongolian herders
- Continental forest steppe
- Traditional ecological knowledge
- Folk habitat
- Landscape ethnoecology
- Herders’ knowledge