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Thursday, 17 November 2016

Folk knowledge of invertebrates in Central Europe - folk taxonomy, nomenclature, medicinal and other uses, folklore, and nature conservation


  • Viktor Ulicsni
  • Ingvar Svanberg and
  • Zsolt Molnár
Journal of Ethnobiology and Ethnomedicine201612:47
DOI: 10.1186/s13002-016-0118-7
Received: 2 June 2016
Accepted: 27 September 2016
Published: 11 October 2016

Abstract

Background

There is scarce information about European folk knowledge of wild invertebrate fauna. We have documented such folk knowledge in three regions, in Romania, Slovakia and Croatia. We provide a list of folk taxa, and discuss folk biological classification and nomenclature, salient features, uses, related proverbs and sayings, and conservation.

Methods

We collected data among Hungarian-speaking people practising small-scale, traditional agriculture. We studied “all” invertebrate species (species groups) potentially occurring in the vicinity of the settlements. We used photos, held semi-structured interviews, and conducted picture sorting.

Results

We documented 208 invertebrate folk taxa. Many species were known which have, to our knowledge, no economic significance. 36 % of the species were known to at least half of the informants. Knowledge reliability was high, although informants were sometimes prone to exaggeration. 93 % of folk taxa had their own individual names, and 90 % of the taxa were embedded in the folk taxonomy.
Twenty four species were of direct use to humans (4 medicinal, 5 consumed, 11 as bait, 2 as playthings). Completely new was the discovery that the honey stomachs of black-coloured carpenter bees (Xylocopa violacea, X. valga) were consumed. 30 taxa were associated with a proverb or used for weather forecasting, or predicting harvests. Conscious ideas about conserving invertebrates only occurred with a few taxa, but informants would generally refrain from harming firebugs (Pyrrhocoris apterus), field crickets (Gryllus campestris) and most butterflies. We did not find any mythical creatures among invertebrate folk taxa. Almost every invertebrate species was regarded as basically harmful. Where possible, they were destroyed or at least regarded as worth eradicating. However, we could find no evidence to suggest any invertebrate species had suffered population loss as a result of conscious destruction. Sometimes knowledge pertaining to the taxa could have more general relevance, and be regarded as folk wisdom concerning the functioning of nature as a whole.

Conclusions

The high number of known invertebrate folk taxa suggests that it would be worth conducting further investigations in other areas of Europe.

Keywords

Ethnozoology Europe Invertebrate fauna Ethnomedicine Nature protection Edible insects

Background

Traditional knowledge systems about the landscape and the biota have been fundamental for human development since the times of pre-modern and pre-industrial societies in Europe. Humans living in close contact with the landscape as herdsmen and peasants have long possessed unified, systematic knowledge, including folk taxonomies, about phenomena that were of importance to them. The use and management of natural resources was based on centuries-old, often millennia-old ecological experience, on multi-generational knowledge passed down from generation to generation [1, 2].
Ethnozoology is the scientific study of the dynamic relationships among people, and animals. Traditional ethnozoological knowledge has great cultural and economical importance. It is widely studied in the tropics and North America (e.g. [3, 4, 5]), but also in Europe (e.g. [6, 7]). Wild animal-based natural resources are often among the key resources local communities depend on [8, 9]. A major goal of these communities is to use and manage these resources sustainably (e.g. taboos: [10]; social rules: [11, 12]). Long-term sustainability in the use and management of natural resources requires healthy ecosystems, while at the same time, sustainable management often contributes to maintaining the health of ecosystems [13, 14].
The knowledge passed by local traditional communities, however, not only serves sustainable use and maintenance of the local community and its environment but may also provide valuable data, information and knowledge to science and conservation. Among the potential benefits of traditional ecological knowledge, it can help science to recognize new species (e.g. [15]), provide data on population sizes and dynamics of species that are difficult to observe [16, 17], support the monitoring of ecosystem health, incl. pasture conditions [18, 19], and develop efficient conservation managament strategies and practices [20, 21, 22, 23].
There is no reason to imagine that European peasant and herder communities differ fundamentally from native societies in other parts of the world with regard to their ecological knowledge [24]. However, there is scarce information about European folk knowledge of wild invertebrate fauna, including their use in healing and nutrition. Researchers in ethnobiology seldom pay attention to invertebrates in the European context [25]. By contrast, several comprehensive studies have been conducted in other parts of the world. As early as 1887, Stearns published an ethnoconchological work on the use of shells as money among aboriginals of North America [26]. This was actually the first time the prefix “ethno-” was combined with a research field, thus preceding Harshberger’s term “ethnobotany”, coined in 1895 [27]. Another pioneering study was Henderson’s and Harrrington’s ethnozoology of the Tewa people in New Mexico. This study gives a full list of animals, including invertebrates, by order and gives their Tewa names as well as their scientific names [28]. In a comprehensive study Bodenheimer [29] reviewed the ethnographical literature of the use of insects as food worldwide. Nowadays there are several important studies available dealing with ethnobiological aspects of invertebrates. We can, for instance, mention Bentley and Rodríguez [30] on the entire invertebrate fauna of Honduras, and Krause et al. [31] on the insect fauna knowledge of the Roviana people (Solomon Islands). Gurung [32] detailed the knowledge of arthropods among Tharu farmers in Nepal, while Hemp [33] described what the peoples living near Mount Kilimanjaro (Tanzania) knew about invertebrates. A particularly impressive ethnozoological study is Morris [34], dealing with the impact of insects and their classification in Malawi folk culture. In addition, the literature on aquatic and coastal-marine invertebrates is particularly rich (e.g. [35, 36, 37]).
The general experience is that many invertebrate species have specific and relevant benefits or detriments, although the number of locally known folk taxa is higher than this [31]. Some culturally salient invertebrate species may even be important keystone species in the lives of certain communities. The majority of these are coastal-marine invertebrates (e.g. shellfish in British Columbia - [37]; crabs (Ucides cordatus) in Brazil - [38, 39]). There are fewer culturally salient species among terrestrial invertebrates, and relatively few species have known folk uses (cf. [32, 40]). Keystone species include, among spiders for example, the bird-eating spiders for Afro-Brazilians in Bahia [41], while among lepidopterans there is the Brahmaeid moth on Taiwan [42].
European folk knowledge about invertebrates has, since the nineteenth century, been researched mostly by folklorists and linguists. In 1879–80 the Swedish author Strindberg used a questionnaire to gather valuable data regarding folk names and rhymes connected with the ladybird. His research, using mapping as a method, is a pioneering work in folklore about animals [43]. An encyclopedia was published about Romanian insect folklore, including local names, legends, fables and myths, the role of insects in witchcraft, and beliefs about insects as pests or as omens [44]. Herman published the local names of insects and invertebrate pest species known by Hungarian herders [45]. We can also mention an interesting article on folk knowledge about botflies (Oestridae) found as parasites on domesticated reindeer, published by the ethnographer and linguist Wiklund [46]. This kind of ethnographic folklore-linguistic research tradition continues today in Europe. Wiggen, for instance, inspired by current ethnobiologists, has recently published an exciting study on the traditional names of lower animals in Norway [47]. In European cultures, it is generally quite uncommon to use or consume invertebrates [48, 49]. The only invertebrates with any significant ethnobiological literature are for the taxa of snails [50], slugs [51], leeches [52], ladybirds [6], crustaceans [53], oil beetles [54] and head lice [55], but none of these are cultural keystone species. Here we should also mention a small but intriguing study on Sami children’s knowledge and use of small invertebrates for amusement and to play with [56]. In 2006, Svanberg [57] published a small book with ethnozoological studies on the human relationship with bumblebees, earthworms, froghoppers, isopods, liver flukes, moonjellies and starfish in Scandinavia and Estonia. There is of course extensive biological literature on pests, but very little detailed documentation of folk knowledge has yet been carried out in Europe [58, 59]. We are, however, of the opinion that further data may exist in local languages, in works on ethnography, local history and perhaps even linguistics, but these have not yet entered the international ethnobiological literature (e.g. [60]).
There is also very little Hungarian literature on folk knowledge of invertebrates. Linguistic (dialectic), ethnographic and ethnobiological literature is available concerning 161 invertebrate species in the Sóvidék region in Transylvania [61], 67 taxa along the Danube [62], the beetle taxa Melolontha melolontha, Lucanus cervus and Lytta vesicatoria [63], and the snail species Helix spp. [64]. Sporadic data may also appear in ethnographic and linguistic literature written in the Hungarian language, for example in monographs on farming and forest ethnography, e.g. in Hegyi [65] on Lytta vesicatoria and Melolantha melolantha. To date, nothing has been published in English about the folk knowledge of invertebrates of the Carpathian Basin.
Our article has the objective of presenting the Hungarian folk knowledge of invertebrate species uncovered in three areas of the Carpathian Basin (in Romania, Slovakia, and Croatia), including:
  1. 1)
    a list of folk taxa of invertebrates,
     
  2. 2)
    their folk biological classifications and nomenclatures,
     
  3. 3)
    their salient features, and
     
  4. 4)
    their uses, related proverbs and sayings, and their conservation.
     
This is the first article in Europe to deal comprehensively with an entire invertebrate fauna. The folk knowledge, nomenclature and uses of 208 taxa are presented in detail. The high number of known folk taxa suggests that it would be worth conducting further investigations in other areas of Europe.

Methods

Study areas

We collected data among ethnic Hungarians practising small-scale, traditional agriculture. Our research was conducted in Romania (Sălaj county [Szilágyság], Nușfalău [Szilágynagyfalu] commune), Slovakia (Gemer [Gömör] region, primarily in the municipalities of Vyšné Valice [Felsővály] and Gemerské Michalovce [Gömörmihályfalva]), and Croatia (Baranja region [Drávaszög], mainly around the villages of Lug [Laskó], Vardarac [Várdaróc] and Kopačevo [Kopács] (Fig. 1)). As the people we studied spend a lot of time in the fields and forests during their everyday activities, they still have a close, direct connection to their natural environment. The settlements where the data were collected, each with between 100 and 2500 inhabitants, are characterised by a large amount of abandoned agricultural land, and by ageing populations.
https://static-content.springer.com/image/art%3A10.1186%2Fs13002-016-0118-7/MediaObjects/13002_2016_118_Fig1_HTML.gif
Fig. 1
The study areas in Central Europe
The three study areas are characterised by a moderate continental climate, with a mean annual precipitation of 600–700 mm. The mean annual temperature in the two northern areas is 8–8.5 °C (July mean 19 °C, January mean −4 °C), while in Baranja, further south, it is slightly higher, around 10 °C (July mean 21 °C, January mean −4 °C) [66]. The elevation is 75–90 m.a.s.l. in Baranja, 200–350 m.a.s.l. in Sălaj, and 190–500 m.a.s.l. in Gemer. Gemer and Sălaj typically have closed broadleaved forests (oak), while in Baranja there is a mixture of riparian vegetation, marshland and mixed hardwood gallery forests (oak, ash and elm).

Data collection and analysis

Data was collected in Sălaj in summer 2010, and in Baranja and Gemer in summer 2012. In each area, the objective was to identify and interview local people with the most extensive knowledge. We employed a number of techniques: in Sălaj we first consulted the local Calvinist priest, and then followed the snowball method; in Gemer we also followed the snowball method, but this time starting with the best informants from earlier ethnobotanical researches; in Baranja we collaborated with the local nature conservation warden, István Tórizs, to meet the people who, in the warden’s view, had the greatest traditional folk knowledge. In total we interviewed 58 people. The overall average age of the interviewees was 75 years (within a range from 36 to 90 years), and the regional average ages were 78 in Sălaj, 74 in Baranja, and 71 in Gemer. All the informants retained memories of traditional forest use and smallholder farming, and some were still practitioners. 55 of the interviewees were Calvinist.
We conducted indoor interviews recorded on a dictaphone (approximately 88 h of recording), since the presentation of living specimens and direct observation of animals in the wild would have been greatly inconvenient for most of the informants. Prior informed consent was obtained before all the interviews, and ethical guidelines suggested by the International Society of Ethnobiology were followed. We studied “all” invertebrate species or species groups potentially occurring in the vicinity of the settlements under investigation. We placed an average of 12 photos of species of similar habitat and size on a sheet of A4 paper, to give interviewees a sense of the context and relative size of each taxon. In many instances during our preliminary study, the differing scale of the pictures had greatly inhibited recognition. Where ambiguous descriptions occurred, further enquiries of the characteristics of the species in question were made in order to facilitate identification of the animal at the finest possible taxonomic level. Detailed lists of invertebrate taxa documented by zoologists were available for the regions studied or for ecologically similar neighbouring regions (e.g. [67, 68, 69, 70]). We also included a few species that do not occur in the areas under investigation, in order to check the authenticity of local folk knowledge.
In total we collected 3465 individual data records on 208 folk generics and specifics. We also conducted semi-structured interviews with the majority of informants and carried out picture sorting, during which they were asked to group species according to their own systems. We used these results to reconstruct the folk taxonomy. Figures depicting taxonomic relations were prepared following the method used by Berlin [71]. Circles drawn in solid lines on these figures indicate scientific taxa (one species, one genus, one order, one family), whereas those drawn in small and large dashes represent, respectively, folk taxa and more inclusive folk categories. When circles of scientific taxa overlap, this indicates that certain scientific taxa were viewed as alike (e.g. “it is a house mouse, but of a different kind”). Inclusive categories were established on the basis of data collected by pile sorting, co-references and direct questions. However, it was not our intention to arrange individual taxa according to Berlin’s system of taxonomic levels, since the communities we examined are too heterogeneous for this. For each of the taxa, where possible, we documented the local name (or names), their salient features, their uses, any damage they cause, any personal attitudes expressed towards the taxa (positive, negative or neutral), and related folklore issues. The habitats of the species (see Appendix) were determined based on the interviews, on our own experiences and on the scientific literature.
We have listed our data in tables, and summarised the results broken down according to informant and taxon. We have not carried out a quantitative comparison of the knowledge among the three communities, for the data sets have, in many cases, low sample sizes. The differences between the three areas which are important from a qualitative aspect are presented in the chapter on results and discussion. Literal quotations are in italics, and comments by individual interviewees are separated by a slash.