IJSL 2012; 218: 145 – 166 DOI 10.1515/ijsl-2012-0062 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 John Wendel and Patrick Heinrich A framework for language endangerment dynamics: the effects of contact and social change on language ecologies and language diversity Abstract: This paper argues for a new perspective on the study of language endangerment dynamics where diversity serves not only as a yardstick for assessing equality, but represents the very basis of equality. To this end, we propose a unified framework accounting for the ecology of languages and language diversity loss. Different ways of economically organizing communities result in power differentials. In cases of contact between them, the language ecologies of the less powerful communities are disrupted through language shift and attrition processes. While these processes have taken place in all competitive language ecologies across time and space, two major waves of language diversity loss can be attested. The first wave began 11,000 years ago following the Neolithic revolution when agrarian societies expanded into the territories of hunter-gatherer communities. The second wave was initiated by the French Revolution when dynastic realms transformed into modern states. The promotion of language nationalism and social mobility in societies imagined to be linguistically homogenous undermined the value and utility of minority languages. Two basic possibilities exist for maintaining linguistic diversity: one is limiting contact to dominating communities; another is finding ways of regulating inter-community relations by mechanisms that do not rely on power alone. Ongoing processes in glocalizing societies suggest that a combination of both options may become a viable way to halt language diversity loss. 30 Keywords: language ecology; language contact; language shift; language attri31 tion; inequality 32 33 34 John Wendel: Dokkyo University, Japan. E-mail: [email protected] 35 Patrick Heinrich: Dokkyo University, Japan. E-mail: [email protected] 36 37 38 39 40 &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 146 1 Introduction 1 In this paper we propose a unified perspective for the study of language diversity loss. Our framework provides both an explication of the general mechanisms at work in language diversity loss and insights into the conditions necessary to sustain language diversity. Language diversity loss refers here to (1) the decline of language use through processes of language shift, and to (2) the erosion of knowledge and the underlying linguistic devices that structure knowledge, that is, language attrition. Research on the loss of language diversity typically treats these dimensions separately. In addition, a focus on either specific geographical regions or periods in history is also found in language endangerment studies. The result of such approaches is inevitably particularistic. Language diversity loss is, in general, the result of changes in language ecologies caused by transformations of the socio-economic organization of communities. In the case of contact between communities with different levels of socioeconomic sophistication, inequalities arise. These inequalities take on different forms across time and space. It is therefore appropriate to differentiate between language ecologies and their socio-economic basis as well as the specific types of socio-economic transitions triggering language shift. Because all processes of language diversity loss are the products of disturbances to ecologies, we begin our paper with a differentiation of the types of language ecologies, followed by a discussion of contact between different ecologies. Lastly, we turn attention to integrating these insights into one unified framework and discussing language endangerment dynamics on its basis. 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 2 Types of language ecologies 26 27 Language ecology emerged as a new paradigm for language studies in the 1970s (Haugen 1972) and grew into a discipline in its own right in the 1990s. The impetus behind the founding of ecological approaches was a felt need to broaden the considerations that account for language contact phenomena. Over the past two decades, scholars such as Mühlhäusler (1996) and Calvet (1999) examined such processes as pidginization, creolization, language spread, shift and attrition from the perspective of ecology. Early on, ecological orientations to language studies led investigators to observe correlations along several dimensions: between the niche-width of languages and latitude, an application of “Rapoport’s Rule”1 to 28 29 30 31 32 33 34 35 36 37 38 1 Eduardo Rapoport observed greater diversity of plants and animals in regions of lower latitudes, that is, in the tropics. &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 39 40 S &6 308 2FWREHU30 147 A framework for language endangerment dynamics 1 language (Mace and Pagel 1995); between biodiversity and linguistic diversity 2 (Harmon 1996), where regions across the planet with high levels of biodiversity 3 had correspondingly high levels of linguistic diversity – research which led to the 4 coining of the expression ‘biolinguistic diversity’ (Nettle and Romaine 2000); and 5 between geographical factors and the diversity of language stocks which were 6 found to be higher in “coastal regions, at lower latitudes, and in wetter and less 7 seasonal climates”, but lower “in continental interiors, high latitudes, and in 8 dryer and seasonal climates” (Nichols 1997: 368). Nettle’s (1996) study offered fur- 9 ther insights into the impact of climate on economies and social networks, dem- 10 onstrating correlations between high amounts of rainfall, longer growing sea11 sons, self-sufficiency of communities, and high language densities. Collectively, 12 this research highlighted the embeddedness of language in the environment and 13 served as the first test cases for ecological orientations. 14 A language ecology refers to a dynamic network of relationships and inter- 15 dependencies between the sociocultural, economic, and environmental contin16 gencies that impact on the use, function, structure, and ways of meaning of lan- 17 guages and their speakers. Two major types of ecologies2 can be identified which 18 we have named “stable” and “competitive” ecologies as in Table 1. Stable ecolo19 gies are best characterized as bottom-up systems in rough equilibrium influenced 20 principally by local conditions (e.g., biogeography, exogamy), whereas competi- 21 tive ecologies are top-down systems associated with punctuation events and in22 fluenced by external conditions (e.g., social and political institutions). 23 24 25 26 2.1 Stable ecologies 27 Stable ecologies are found in “communication communities” (Mühlhäusler 1996) 28 in which the functional relationships between languages complement each 29 other, forming networks of interdependencies. They are called “stable” because 30 the speech varieties making up these communication communities do not com31 pete with one another and are therefore able to coexist side by side. Although 32 stable ecologies are often richly multilingual, the languages within them are in a 33 layered or structured relation to each other (Mühlhäusler 2000). Such layered 34 relations allow for a high “integrity” of such language ecologies – that is, such 35 ecologies are able to carry high language diversity. The languages in stable ecolo- 36 gies have small numbers of speakers (typically constituting hunter-gather bands); 37 38 39 2 This discussion builds on the work of many scholars including Dixon (1997), Mühlhäusler 40 (2000, 2005), Nettle (1999), Nettle and Romaine (2000) and Mufwene (2008). &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 148 Competitive Stable Features – Predominately bottom-up influences – Symmetrical power distribution – Associated with equilibrium states – Predominately esoteric languages and communication – Pre-settlement semantics – Predominantly top-down influences – Asymmetrical power distribution – Associated with punctuation events – Predominantly exoteric languages and communication – Post-settlement semantics Sub-type Features 1 – Migration into unoccupied territory – isolated island and rainforest communities. – Associated with hunters and gatherers, pastoralists. 2 Emergent ecologies 6 Multilingual ecologies – Structured language layers in complementary relation to each other – diversity sustaining processes. – Associated with hunters and gatherers, pastoralists. – Includes multilingual exotic-endemic communities. Replacement ecologies Exploitation ecologies Glocalizing ecologies – Language replacement – total collapse and replacement of less powerful language groups by dominate language groups. – Associated with settlement colonialism, empires. – Language shift to and expansion of dominant languages. – Policies and ideologies undermine the vitality of minority languages. – Associated with exploitation colonialism and nation states. – Language spread and language revival. – Pluricentric languages, nativization. – Novel forms of contact and competition; strategies for language maintenance and revival; exaptation of infrastructures and communication technologies. – Associated with globalization, transnational migration, plurilinguistic urban centers. 4 5 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 Table 1: Types of language ecologies 32 small numbers of speakers mean that no one community enjoys significant advantages in economic or technological strength over another. For this reason, stable ecologies are in an equilibrium state (Dixon 1997) with roughly the same number of languages spoken in any given area over long periods of time. Because of their small sizes, communication communities in stable ecologies are highly susceptible to local conditions and pressures (i.e., bottom-up processes) such as climate change and changes in social organization. &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 3 33 34 35 36 37 38 39 40 S &6 308 2FWREHU30 149 A framework for language endangerment dynamics 1 As Table 1 shows, there are two sub-types of stable ecology: emergent and 2 multilingual ecologies. Emergent ecologies are manifest when a community 3 moves into an unoccupied territory. Multilingual ecologies communities are typi- 4 cally distinguished by high levels of multilingualism and by layered networks of 5 speech varieties. Multilingual ecologies have been documented, for example, in 6 New Britain (Thurston 1987), New Guinea (Kulick 1992; Laycock 2001 [1991]), or in 7 the Amazon Basin (Kaufman 1990). Also included in stable multilingual ecologies 8 are those regions constituted before European intrusions that include a mix of 9 exotic-endemic languages. Exotic-endemic ecologies can be found, for example, 10 in the Brazilian Vaupés region in the Amazon (Aikhenvald 2010), Timor (Hajek 11 2000), and along the north coast of Papua New Guinea where we find Austrone12 sian and Papuan languages side by side (Mühlhäusler 2000). 13 14 15 16 2.2 Competitive ecologies 17 Beginning around 11,000 years ago, the practice of agriculture initiated indepen18 dently by populations in several parts of the world set the scene for technological 19 innovation and socio-economic change. These developments initiated the transi- 20 tion from hunter-gatherer bands to larger, more sophisticated political units and 21 lay the groundwork for power differentials between the “haves” and “have nots” 22 – the cornerstone of competitive ecologies. 23 Competitive ecologies are found throughout the modern world today. In 24 contrast to the egalitarian social structure of hunter-gatherer communities 25 (Woodburn 1998 [1981]), the social organization in competitive ecologies is pre26 eminently hierarchical. The nation-state represents the present-day apex of the 27 development of competitive ecologies. Competitive ecologies are thus impacted 28 by pressures and events generally outside the control of local communities. If 29 smaller languages are not displaced immediately, language shift results in having 30 dominant languages grow at the expense of minority languages, and language 31 attrition results in reductions of domain use and linguistic structure. Major punc32 tuation events that result in competitive ecologies include the development of 33 writing systems, the spread of literacy and printing, scientific and technological 34 advances, the industrial revolution, nation-state building, and the emergence of 35 standardized languages. All these events coincide with language diversity loss 36 or with marginalization of smaller language varieties into geographic or societal 37 peripheries. 38 There are three sub-types of competitive ecology: replacement, exploitation 39 and glocalizing ecologies. Each type is characterized by a major process of lan- 40 guage change: as indicated in Table 1, replacement ecologies are characterized &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 150 by language replacement, exploitation ecologies by language shift, and glocalizing ecologies by language spread and grassroot efforts aimed at language revival. Total collapse and replacement of indigenous language ecologies caused by the spread of disease or genocide are characteristic of replacement ecologies. These histories are often associated with settlement colonialism as discussed in Mufwene (2008). North America and Australia are obvious examples of replacement ecologies where today pockets of relic languages, typically on native “reservations”, are surrounded by larger transplanted languages such as English, Spanish and Portuguese. Exploitation ecologies are driven principally by economic inequalities: an established dominant language, due to its higher social status and economic advantage, undermines the vitality of other languages in contact encounters. The result is a shift away from small local languages to the languages of prestige, often in a matter of generations. Exploitation ecologies are characteristic of histories associated with the industrial revolution (Nettle and Romaine 2000) and exploitation colonialism (Mufwene 2008). Finally, glocalizing ecologies are a consequence of globalization processes such as global communication networks and infrastructures, new media, and changes in migration patterns. Among many post-industrial countries, there is a growing sense of awareness of the rights of ethnolinguistic minorities to the practice of their cultures and to the transmission and use of their heritage languages in these ecologies. Virtual language contact and communities have emerged, creating new domains of language use, and new possibilities to circumvent competition with dominant languages (Eisenlohr 2004). While it is true that in glocalizing ecologies, larger languages such as English and Spanish have spread to an unprecedented extent, it is significant that such languages are typically learned as a second language at school and are often adapted to regional or local circumstances and identities over the course of several generations (García 2001). Thus typically, we see two opposing processes at work in these ecologies: dominant language spread on the one hand, and language revival on the other. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 2.3 Meaning-making in pre- and post-settlement ecologies Little attention has been paid to the roles that ecologies have played in supporting the ways languages can mean. The idea here is that language ecologies are distinctive not only in terms of the bottom-up/top-down processes that predominate in each ecology, but also in terms of their potential for promoting and sustaining distinctive ways of meaning creation – the linkages between social orga- &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 33 34 35 36 37 38 39 40 S &6 308 2FWREHU30 151 A framework for language endangerment dynamics 1 nization on the one hand, and linguistic structure and semantic development on 2 the other. 3 Thurston’s (1987) work in New Britain, Papua New Guinea, led him to observe 4 two types of language: esoteric languages (complex languages used for commu- 5 nication within communities) and exoteric languages (less complex languages, 6 including regional lingua francas and pidgins, used for inter-group communica- 7 tion). He noted that languages on the esoteric side of the continuum were often 8 deliberately made to be difficult for adult learners, a process he called esoter9 ogeny, thus securing their value as badges of community identity. Exoteric lan- 10 guages tended to have larger numbers of speakers and were more readily learned 11 by adults. In ecological terms, esoterogeny can not only account for high levels of 12 linguistic diversity, but also for the perpetuation of languages with small speaker 13 populations situated in areas of high linguistic diversity. The upper layers in 14 the hierarchy of languages in a communication community, in effect, protect the 15 local languages. A process such as esoterogeny would be unsustainable in a com16 petitive ecology. 17 The esoteric-exoteric language continuum was confirmed in a statistical 18 analysis of 2,236 languages in a study by Lupyan and Dale (2010) using combined 19 demographic and morphological language variables. They showed that lan- 20 guages with smaller speaker populations spoken over smaller areas and having 21 less contact with other language communities have overall simpler morphologi22 cal systems than languages having larger speaker populations, greater geograph23 ical coverage and greater language contact. Their Linguistic Niche Hypothesis pro- 24 vides that “the level of morphological specification is a product of languages 25 adapting to the learning constraints and the unique communicative needs of the 26 speaker population” (Lupyan and Dale 2010: 7). 27 These and other insights into the relationships between social and linguistic 28 structure have been elaborated by other investigators (e.g., Sampson, et al. 2009; 29 Trudgill 2011). For example, Wray and Grace (2007) developed a position based 30 on the juxtaposition of a societies of intimates and a societies of strangers, pro31 posing that early human languages, i.e., those of the hunter-gatherer cultures, 32 and the communicative mode that characterized their interactions, were primar- 33 ily esoteric, while modern human languages and their communicative mode are 34 primarily exoteric. “Languages that are used predominately for esoteric (intra35 group) communication tend to have features that are semantically and grammat36 ically ‘complex’, while those used also (or even exclusively) for exoteric (inter37 group) communication become ‘simplified’ towards rule-based regularity and 38 semantic transparency” (Wray and Grace 2007: 543). It is only larger political or 39 economic units (i.e., those of the post-settlement societies) that bring people into 40 extensive contact with strangers. Contact with strangers means that “societies of &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 152 intimates” cannot rely on the same high degree of implicitness in their interactions for maintaining comprehensibility between speakers and hearers. The need to be more transparent pushed languages toward greater explicitness – less irregularity, a higher degree of predictability and more rule-governed – in a word, compositional. Thus Wray and Grace find that over time, greater compositionality in language is one consequence of talking with strangers. Very much related to structural complexity, another dimension along which ecologies support meaning-making in languages is the semantic dimension. Halliday (2001 [1990]) sketched out the linguistic consequences of transitions from one type of socioeconomic organization to another, positing a view of grammar as theories of experience. Languages – their use, functions, underlying semantic and structural organization – are neither the product of some universal blueprint set deep eons ago within the minds of speakers, nor are they mirrors passively reflecting changes in sociocultural and material conditions. Instead languages are at the “intersection of the material with the symbolic” (Halliday 2001: 179) where meaning making is forged. Along these lines, Halliday proposes a “semogenic” history of language – that is, a historical account of the processes of construing meaning. Halliday (2001: 181–183) proposes four major stages, each period culminating in an upheaval in the ways of meaning: (1) the hunter-gatherer stage, (2) the settlement stage, (3) the iron-age culture stage and (4) the modernity stage. For example, in his view of grammar as theories of experience, Halliday (2001: 181) posits a shift from pre- to post-settlement semantics, through which abstract meanings shifted from the “interpersonal towards the ideational – from, for example the rights and duties of kinship to generalizations about the phenomena of experience, and within the ideational, from processes towards things.” Things became “construed as commodities, they take on value, they can be itemized and drawn up in lists”. These shifts are manifested in language by the nominal group: “nouns measured into quantities, assigned qualities along various scales, organized into taxonomies of classes and subclasses, social relations transformed into institutions.” Two conclusions can be drawn from the above discussion. The first is that the ecologies and languages across the pre- and post-settlement divide provide for distinctive meaning creation potential which, in turn, leads to differently textured views on the world. The second is that when ecologies are disturbed and when pressures, from whatever sources, effect changes that cause transitions from one ecological configuration to another, it is not just language size, power, and prestige that are affected, it is also the underlying structural and semantic properties of languages that shift to accommodate new sociocultural and economic contingencies – contingencies themselves made possible only through semiotic mediation of the environment. &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 S &6 308 2FWREHU30 153 A framework for language endangerment dynamics 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 3 Contact and transition across language ecologies There are two general release mechanisms triggering the transformation from one type of socio-economic order to the next. One is contact with and dominance by another community or society, which subsequently imposes its economy, social organization, values, etc.; the second is what David Nettle (1999: 79) calls “managing ecological risk”. Simply put, different types of societies vary because they cope in their own way with ecological risk in order to assure their survival and wellbeing. Hunter-gatherers primarily cope with ecological risk by fission and mobility, agriculturalists with storage and exchange, dynastic realms with expansion, modern societies by ideological mobilization of its members, and glocalizing societies by attention to sustainability and exaptation of novel infrastructures and information technologies. Let us consider the transition between these socioeconomic types in more detail. 17 18 19 20 3.1 The socio-economic basis of hunter-gatherer languages 21 Before the Neolithic revolution, all communities depended entirely on local 22 plant and animal resources for their survival. Typically, locally available re23 sources support only small bands, and once the resources are depleted, the 24 groups will splinter and move in search of new territories. These bands are homo25 geneously constituted and enjoy a strong sense of group membership (see e.g., 26 Marshall 1998: 65). There is no or little social stratification or occupational spe27 cialization. Thus day-to-day interactions within the community are grounded in 28 a shared knowledge, and shared behaviors and understandings, with little need 29 to be explicit. 30 Pre-settlement cultures are also oral. Speech is ephemeral, limited both in 31 time and space. Apart from orally transmitted histories and myths that are struc32 tured for ease of memory, they have no recourse to aide memoires. In his study on 33 the transition from oral to literate cultures, Ong (1982) shows how expression in 34 oral cultures is additive rather than subordinative, aggregative rather than ana- 35 lytic, contextualized in the here-and-now rather than abstract, and participatory 36 rather than distant. Unable to organize knowledge in the elaborate and abstract 37 taxonomies, as is possible with the technology of writing, speakers of unwritten 38 languages rely on mnemonic strategies to structure their knowledge. From our 39 literate perspective, these pre-literate practices appear to place heavy restrictions 40 on the form and structure of languages. &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 154 One well-known case of restricted structural complexity concerns the Pirahã language spoken by some 350 people in western Brazil. Everett (2005) has found only four words indicating time relationships in Pirahã; no numerals or system of counting, but instead two words meaning ‘relative large amount’ and ‘relatively small amount’; no color words; the simplest kinship system ever recorded for a language; and, significantly, no recursion, a combinatorial rule that allows for embedding in language. The Pirahã have also remained stubbornly monolingual despite 200 years of contact with Brazilian Portuguese speakers. Everett explains that many of the phenomena above can be explained by a single cultural value that the Pirahã place on immediate experience that constrains not just their way of living, but the Pirahã grammar as well. Everett (2005: 633) concludes, “Pirahã thus provides striking evidence for the influence of culture on major grammatical structures. . . . If I am correct, Pirahã shows that gross grammatical properties are not only correlated with sociocultural facts but may be determined by them.” How might such a language look after a transition to post-settlement conditions? 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 3.2 Transition to agricultural societies 19 Many indigenous hunter-gatherer communities disappeared and transformed under the advance of the first agriculturalists, spreading from southwestern and East Asia, northern and central Africa, and Central America. The result was a first wave of language diversity loss. Shifting the socioeconomic system from hunting and gathering to farming resulted in previously unknown types of societies, settled in fixed places, with a complex division of labor, technological innovation, surplus food production, trade, and social stratification. All of this required new institutions and forms of knowledge for the regulation of daily life. Consider two examples of recent transitions away from hunter-gatherer traditions. In his study of ethno-botanical knowledge among the Piaroa in Venezuela, Zent (2001: 207–209) observed a loss of ethno-botanical knowledge in their acculturated riverine habitat. In the 50 years that the Piaroa migrated away from their traditional lands in the high hills between rivers, their knowledge retreated along with declining competence of their language. Spanish has become both the dominant language of choice and the chief medium for knowledge of the world. Crawhall (2008), an authority of the Khoe-San hunter-gatherer societies, explains that “hunter gatherer peoples manage their knowledge in substantially different ways than other systems or other economic modes.” For example, ecological knowledge is coded in social relationships. He has observed disturbances to the chain of knowledge transmission, by habitat destruction or &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 S &6 308 2FWREHU30 155 A framework for language endangerment dynamics 1 forced removal off the homelands, that have caused a change in communicative 2 relationships, which in turn, changed “the ability to diffuse the knowledge and 3 keep it in circulation.” Crawhall (2008) asks the very excellent question: “Is it 4 possible to move from a hunter-gatherer language with a highly diffused, very 5 detailed knowledge of biodiversity to a pastoralist or agriculturalist language, 6 and still be able to manage the same knowledge composition?” Clearly, the an7 swer is, “no”. 8 9 10 11 3.3 From dynastic realm to the nation state 12 What Anderson (1991) calls “dynastic realms” do not constitute societies in the 13 strict sense because a “sense of belonging” is not equally shared among all in- 14 habitants, nor is such a sense of belonging actively being promoted as in the case 15 of nation building. In this paper the term “dynastic realm” refers to various pol16 itical economies such as chiefdoms, pre-modern kingdoms, and empires. Dynam17 ic realms play a significant role in the growth and spread of specific languages. 18 Growing languages in dynastic realms serve as vehicles for the spread of reli19 gions, knowledge and legal systems. Although still based on an agricultural 20 economy, dynastic realms feature occupational specialization and urbanization, 21 and this affects again language patterns and use. To start with, cultural special- 22 ization and stratification results in specialized vocabularies, which need to be 23 managed and updated. Dynastic realms also require standard measurements due 24 to their progress in agriculture and long-distance trade. Most crucial with a view 25 to language diversity, however, is an established division of work between elite, 26 sacred or classical languages, that is, written languages on one hand, and of un- 27 written vernacular languages on the other. As a result thereof, language does not 28 lay ready as a resource to create one imagined community within the dynastic 29 realm. Dynastic realms are limited by frontiers, rather than borders beyond which 30 the Other resides. That is to say, the transition from the familiar to the unfamiliar 31 is more gradual than in the case of modern states. Consequently, dynastic realms 32 have a clear distinction between the center and the periphery, the latter of which 33 grows increasingly unfamiliar the further away one gets from the center. Rather 34 than being united in and through language, diglossia or societal bilingualism in 35 dynastic realms results in having literacy being restricted to the ruling elite. As an 36 effect, the vitality of regional languages is often left intact and language ecologi37 cal integrity remains high. 38 In contrast, modern states represent a new dramatic departure of social 39 and linguistic regimentation. Modernization goes hand in hand with industri40 alization, urbanization, the unification of a national labour market and social &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 156 mobility. The modern state serves as the main centre for regulating and reproducing society into a consistent and uniform direction. Typically, large communities become imagined as homogenous and uniform, from border to border, irrespective of center or periphery. While the territory governed by dynastic realms is delimited by the results of sexual politics, that is, arranged marriages between ruling elites, the borders of the nation state are seen as the quasinatural territory inhabited by the quasi-natural entity of the nation. In order for this to happen, the conflict between the subjective antiquity and primordial imagination of the nation and the historical novelty of the nation needs to be confused by ideology (Anderson 1991: 5). Unifying nations in terms of language, that is, making nations where there were none before by linguistically unifying inhabitants of a given territory, became a prime task of modernity. In contrast to dynastic realms with their indifference to language diversity among their subjects, the socio-cultural periphery in modern states comes under pressure to assimilate in the process of nation building because nation states highlight unity within state borders and project diversity to the outside. All those falling between the gap of the nation as the invention and its multilingual makeup come under pressure to adapt to the imagined model. Language diversity loss is the result. Consider the example of Spanish in the Americas. At the start of the 19th century, Spanish speakers were outnumbered by a ratio of 3:1 by speakers of indigenous languages. It is only after gaining independence from the Spanish crown, that is, after shifting from a dynastic realm to a modern state, that Spanish spread there to the extent that basically everyone speaks Spanish now in the former Spanish colonies, and that nine out of ten of Spanish speakers are first language speakers (Ostler 2005: 373–376). Likewise, the spread of Russia in Siberia (Salminen 1997) and that of French in what is today France (Marcellesi and Larousie 1997) gained a whole different quality only after the rise of modernity there. Heinrich (2012) offers a book-length discussion how the Japanese nationbuilding process has been threatening Ainu, the Ryukyuan languages, Ogasawara Creole English and Japanese Sign Language in Japan. Language diversity loss in nations where the replacing language is always the dominant state language3 deserves our attention because this constitutes the second wave of language loss. Language diversity is diminished because modernism introduces the novel idea of equality through national unity and seeks to attain it through uniformity, 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 3 Given the fact that “national language” is an ideological construct, we term it here as what it 39 40 is, a “state language”. &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS S &6 308 2FWREHU30 157 A framework for language endangerment dynamics 1 that is, aligning everyone to the dominating language, culture, history and mores. 2 Efforts aiming at upward social mobility often lead to the adaptation to dominant 3 language and culture, and renders dominated languages largely without signifi4 cance in modern orders. To be sure, such a situation is not egalitarian from the 5 perspectives of dominated communities. 6 7 8 9 3.4 Glocalizing societies 10 All the effects of economic globalization on daily life are necessarily locally an11 chored. Globalization is already locally internalized because the changes intro12 duced by economic globalization run through local institutions. Together with 13 transnationalism and cosmopolitanism, glocalization results in societies where 14 the globe is increasingly often regarded as the main point of reference. The dis- 15 course on language endangerment in many states across the world is in itself 16 such an example. At an abstract level, such reflections result in new assessments 17 of issues such as pluralism, variety, contingency and ambivalence. Modernity 18 saw such characteristics as failures, and thus as issues to be corrected, a view 19 no longer tenable to many today (Bauman 1992: 187–188). Ensuing from such epis- 20 temological change are also conflicting views on language use and language 21 diversity. 22 We are witnessing in glocalizing societies an increase of linguistic diversity in 23 modern states through transnational migration, a new kinetic elite working in 24 institutions of global management and knowledge, and language revitalization 25 efforts, and all of these developments are in themselves contributing to a new 26 linguistic diversification. Code switching, language crossing, migrant varieties 27 of host-society languages, and national varieties of world languages are also part 28 of this new diversification wave in glocalizing societies. Since modernist institu- 29 tions are largely left intact, we arrive thus at the situation where we encounter a 30 defense of language nationalism, a revival of regional languages and cultures, a 31 diffusion of migrant languages, the unprecedented spread of international lingua 32 francas, and new extents and forms of language hybridization. 33 In view of the many concurrently occurring changes, the study of language 34 endangerment dynamics becomes indeed a challenging undertaking. A state like 35 Brazil, for example, has the greatest share of the estimated 100 uncontacted 36 tribes remaining in the Amazon Basin (Pantone 2008). There are also stable mul37 tilingual communities among the indigenous groups there (Aikhenvald 1999). 38 At the same time, the government is displacing thousands of indigenous peo39 ple every year in its rush to access energy resources. The construction of infra- 40 structure such as the Belo Monte Dam, the raising of new settlements, and the &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 158 movements of thousands of Brazilian Portuguese speakers to work on construction projects are triggering radical alterations that transform the language ecologies of entire regions. As the sixth largest economy in the world, Brazil is at the same time subject to the effects of economic globalization. Glocalization ecologies, on the one hand, contribute to the spread of English and Spanish, but on the other hand, in these same ecologies efforts to maintain or revitalize endangered languages are also promoted. While the Brazilian government in 1996 mandated foreign language instruction (mainly Spanish and English) for grades 6–12, government recognition of the rights of indigenous peoples to their language and culture is pushed ahead (Hornberger 1998), and grassroots efforts to maintain the languages of ethnolinguistic minorities are initiated (Rohter 2005). In terms of language ecologies, Brazil represents a complex case. In her discussion on the difficulties in separating out one linguistic area from another, Aikhenvald (2001: 168) writes that the “Amazon can be compared to a set of Chinese boxes of linguistic areas and subareas, included within each other”. Understanding how such ecological mosaics interact is one of the challenges facing the study of language endangerment dynamics today. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 4 The study of language endangerment dynamics Languages emerge, spread, decline, and disappear, all within the context of the ecologies that shape them, and languages, in their turn, have a crucial role in shaping ecologies. Languages and their speakers are players in an incessant dynamics that is grounded as much in human behaviors and human histories as it is in environmental and biogeographical contingencies. Thus, the study of language endangerment dynamics needs not only to account for language shift and language attrition in the context of their ecologies, but it also has to relate to the fact that ecologies have different historical trajectories, partly as an effect of the region in which they are embedded; that ecologies may be layered in relation to each other in complex ways; that ecologies are successional from the perspective of history, but that many present-day conditions create non-successional contact encounters; and that competitive ecologies are by far the most pervasive today. What is more, phenomena such as exotic-endemic, post-settlement and presettlement semantics, written and oral language are not neutral labels but powerloaded phenomena. The former always dominate the latter. Thus, two issues are at the heart of change in language ecologies: (1) the changing socio-economic basis of language ecologies and (2) the relations of domination and inequality in contact between communities, that is, the power-differentials resulting from different socio-economic types of organization. &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 S &6 308 2FWREHU30 159 A framework for language endangerment dynamics 1 2 3 4.1 The community – society continuum in language endangerment dynamics 4 The socio-economic types discussed above differ dramatically in terms of their 5 complexity. This has not only repercussions on the language ecologies, but on 6 all institutions regulating daily life. Ferdinand Tönnies’ (2007 [1887]) classical 7 distinction between community (Gemeinschaft) and society (Gesellschaft) cap8 tures many of these differences quite well. His two concepts form a continuum, at 9 which the community end correlates with bottom-up regulations from within net- 10 works, manifesting in culture, folkways or mores. Daily life is mainly regulated 11 by concord and kinship. Direct influences on community also include climate 12 and locally available flora and faunal assemblages. At the society end of this con- 13 tinuum, regulation of everyday life correlates with numerous pressures originat14 ing from outside personal and community networks. Such top-down regulation 15 takes the form of legislation, rationalized in various ways such as religion, schol- 16 arship, or public opinion. Daily life is embedded in large imagined communities, 17 which are regulated on the basis of conventions, laws and rights. 18 19 20 21 22 4.2 The inequality/equality continuum in language endangerment dynamics 23 Domination and inequality are part and parcel of all competitive ecologies. It is 24 this, which leads Coulmas (2005) to observe that competition between speech 25 communities based on economic, political and cultural strength benefits the 26 strongest player almost without fail. Unsurprisingly therefore, it is the disempow27 ered who find themselves in situations where maintaining their languages and 28 cultures is difficult (Kymlicka 1995). Contact on the basis of inequality is the major 29 cause of language diversity loss across all types of socio-economic orders, and 30 language is one of the dimensions in which inequality is manifest in competitive 31 ecologies. While indeed no language “has a privileged window into reality” 32 (Nettle and Romaine 2000: 62), one nevertheless needs to add that some languag33 es offer their speakers access to ways of meaning-making and worldviews that 34 heavily leverage their odds against speakers of other languages. In this sense, 35 languages themselves may serve as instruments for domination, because lan- 36 guages of ecologies differing from the dominant group are ill-adapted to the 37 newly imposed sociocultural environment. As a consequence, pre-settlement 38 speakers and their languages, for instance, may be perceived to be backward, and 39 this view then serves as a rationale for not granting such communities autonomy, 40 that is, it serves as a rationale for dominance. From this vantage point it is the &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 160 business of minority communities to find ways to adapt to the dominant society. 1 As we have seen above, language shift is a strategy often resorted to in such 2 constellations. 3 4 5 4.3 The field of language endangerment dynamics 6 Changes in language ecologies driven by both social change and inequality in contact cause language diversity loss. The field of language endangerment dynamics is thus located at the juncture of the community/society and inequality/ equality continua as in Figure 1. It follows that language ecologies can be identified within the crossed dimensions and that distinct levels of socio-economic organization and degrees of equality in contact can be located at specific points. Stable language ecologies (e.g., hunter-gatherers) are thus found in cell A where human groups are small in number, social networks are multiplex, and in which political structures are comparatively horizontal whereas, at the other extreme, competitive ecologies (e.g., dynastic realms, modern societies), located in cell C, represent conditions where the groups are organized in far greater numbers and the political structures are hierarchical. Cell B represents ecologies in transition (e.g., early agriculturalists, exotic-endemic language communities) between sta- 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 Fig. 1: Language endangerment dynamics &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 40 S &6 308 2FWREHU30 161 A framework for language endangerment dynamics 1 ble and competitive ecologies, and cell D, represents the potential of glocalizing 2 ecologies, in which we find elements of both competitive and stable ecologies 3 strongly represented. 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 Figure 1 clarifies that there are three basic language replacement scenarios, with the replacing language either being an agriculturalist language, a language of a dynastic realm, or a national state language. These scenarios and their corresponding shifts (Shift 1, 2 and 3 in Figure 1) are prefigured in earlier sections of our paper above. Thus, Shift 1 corresponds to displacement of hunter-gatherers by more powerful farming populations. Because of their inferior numbers and early-stage technologies, hunter-gatherer communities and their languages are easily driven out when brought into contact with successful agriculturalists (i.e., those who have overcome the “equilibrium trap”, Nettle and Romaine [2000: 108]). The spread of farming populations coincides with the extinction, expulsion or assimilation of hunter-gatherer communities. Shift 2 corresponds to the expansion of empires and their languages in which diseases and military technologies play a significant role in language replacement scenarios. And Shift 3 is fueled largely by economic factors and nationalist ideologies through which language shift away from minority languages to state languages and from multilingualism to monolingualism are taken as signs of progress. Additionally, the specific coordinates of a given language ecology within the crossed dimensions allows for a characterization with regard to the ecology’s stability and for predictions of its prospects, and provides for a heuristic means to identify ways of maintaining language diversity. In this regard, Figure 1 points to two fundamental scenarios for endangered language communities. The first option is to strive for more equality and seek liberation from coercion and ideological dominance. This is where language maintenance activities become an emancipative endeavor, a call for social change, usually loaded with political conflict. The second option is to reduce contact. This is where language maintenance activities become involved in quests for more autonomy, one way of which may also include the formation and expansion of new close-knit endangered language networks. The framework in Figure 1 also suggests ways for generating insights into the dynamics of endangered languages, including distinguishing between the types of shifts above; understanding better the interactions between layers in layered language ecologies which result from such shifts; tracking and explaining the changes that linguistic structures and communication communities undergo when shifting from one ecology to another; better characterizing the features and processes of non-successional shifts (e.g., hunter-gatherers shifting directly to state language); and coming to grips with the new and emerging patterns and potentials in glocalizing ecologies. Given that most endangered languages today &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 162 face non-successional transition scenarios, this should certainly be one main focus of future study. We have referred above to two such instances, one involving the Piaroa (Zent 2001) of Venezuela and the other, the Khoe-San (Crawhall 2008), and there are a multitude of other contact encounters between hunter-gatherer communities and the apparatus of modern states around the world. What particular challenges do non-successional transitions present to speakers of huntergatherer languages? How is it that communities such as the Pirahã of Brazil have apparently managed to forestall efforts to have them assimilate to the mainstream culture? Another focal area for research should be centered on the transitions from modernist to glocalized ecologies as indicated in Figure 1. Glocalized environments differ from the ecologies envisaged by modernists and thus testify to the increasing difficulties to regiment languages along modernist lines. The highly multilingual urban centers (see e.g., Extra and Yagmur 2004) we find across the world today contradict modernist ideologies that intertwined language, nation, and territory and presented this constellation as the natural order of things. Relaxing this linkage has allowed for a “return of the social”, part of which includes the linguistic diversity of a diversifying population. The emerging glocalized ecologies differ in many important respects from all other ecologies. These differences include the revitalization of endangered indigenous languages – a phenomenon which came to be termed “reversing language shift” (Fishman 1991). Perhaps misunderstood in some quarters, reversing language shift does not promote a “reversion” to old orders, but is a push forward to overcome restrictions and limitations of modernist institutions, which clears the way for the emergence of new ecologies. Given the dynamic between social and linguistic structure described above, we can expect languages to shape, and be shaped by, innovations made to the sociocultural and technological environments: as novel social interactions and communication media are innovated, new varieties, registers and forms of discourse emerge while established ones fall out of use. Control and regulation of these newly formed communication communities becomes increasingly difficult. What is more, in a number of contexts, such control and regulation no longer has the prominence it has once enjoyed. The linguistic mosaics that characterize urban centers today favor the dominant languages within these ecologies which, however, in contrast to the past, tend to be promoted as second or additional languages that function as lingua francas rather than as languages of national identity. What all of these individual developments amount to is a new process of layering between languages in environments where locality loses its previous significance as it transforms into a site of coexisting worlds. That said, it becomes clear that many glocalized environments are not community-oriented places in &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 S &6 308 2FWREHU30 163 A framework for language endangerment dynamics 1 the traditional sense. New communities of practice replace neighborhoods as mi- 2 grants to glocalized ecologies deal with ecological risk by having placed individ- 3 ual wellbeing above remaining within their home communities. The subsequent 4 sense of loss fuels a longing for community and constant efforts to rebuild it on 5 the shifting sands of glocalized ecologies (Bauman 2000). The implications for 6 research on glocalized ecologies are that new concepts and analytical tools are 7 needed: networks rather than domains, metro rather than ethnic, individual tra8 jectories rather than communities must be at the fore of such research. 9 10 11 12 5 Conclusion 13 In a reassessment and defense of Whorf’s writings on language diversity, 14 Fishman (1982: 13) pledged 30 years ago to forego the narrow perspective of 15 “linguistics-as-a-science”, arguing that “linguistics is also very significantly a 16 humanities field and an applied field as well”. With regard to language endan- 17 germent dynamics this requires relinquishing the perspective of the dominant 18 society on the dominated, because dominance is the very source of the issue 19 under study. One needs to stop self-evidence mediated by dominant ideology as 20 proof of the naturalness and appropriateness of power differences and inequali- 21 ties. Minority issues require minority perspectives, endangered languages require 22 endangered language perspectives, hunter-gatherer ecologies require a hunter23 gatherer perspective, and so on. Such an attitude is at the present, however, not 24 fostered in agrarian societies, or dynastic realms, or modern societies. It is also 25 not widely practiced in modern scholarship, a central pillar of modern society. 26 In order to maintain language diversity and to support endangered lan- 27 guages, scholars have mainly stressed the cognitive benefits of individual bilin- 28 gualism (Wurm 2002) and the societal benefits of language diversity (UNESCO 29 2003). However, because the main trigger of language diversity loss is power im- 30 balance, all attempts to maintain linguistic diversity not taking this factor into 31 account are doomed to achieve little in uncovering the language loss mechanisms 32 and the possibilities to counter them. Fishman (1991: 411) rightly said that revers- 33 ing language shift “implies remaking social reality”. As long as these issues are 34 not identified in research into endangered languages and addressed in mainte- 35 nance efforts and language policies, communities on the shorter end of the power36 divide will continue to undergo language shift and language attrition. What is 37 needed is scholarship that takes as its point of departure minority perspectives 38 and issues in an effort to develop greater insights into the dynamics of language 39 endangerment. Such direction of sociolinguistic research will demonstrate in 40 more detail that equality in diversity are in fact two sides of the same coin. &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 164 References 1 2 Aikhenvald, Alexandra Y. 1999. Areal diffusion and language contact in the Içana-Vaupés basin, North West Amazonia. In R. M. W. Dixon & Alexandra Y. Aikhenvald (eds.), The Amazonian languages, 385–415. Cambridge: Cambridge University Press. Aikhenvald, Alexandra Y. 2001. Areal diffusion, genetic inheritance, and problems of subgrouping: a North Arawak case study. In Alexandra Y. Aikhenvald & R.M.W. Dixon (eds.), Areal diffusion and genetic inheritance: problems in comparative linguistics, 167–194. Cambridge: Cambridge University Press. Aikhenvald, Alexandra Y. 2010. Language contact in Amazonia. Cambridge: Cambridge University Press. Anderson, Benedict. 1991. Imagined communities, 2nd revised edn. London: Verso. Bauman, Zygmunt. 1992. Intimation of postmodernity. London: Routledge. Bauman, Zygmunt. 2000. Community. Cambridge: Polity Press. Calvet, Louis-Jean. 1999. Pour une écologie des langues. Paris: Plon Publishers. Coulmas, Florian. 2005. Changing language regimes in globalizing environments. International Journal of the Sociology of Language 175/176. 3–15. Crawhall, Nigel. 2008. Endangered languages and traditional ecological knowledge: Part 1. Presentation delivered at the American Museum of Natural History, NY, 3 April. http://symposia.cbc.amnh.org/biocultural/agenda.html (accessed 15 December 2011). Dixon, R. W. M. 1997. The rise and fall of languages. Cambridge: Cambridge University Press. Eisenlohr, Patrick. 2004. Language revitalization and new technologies. Annual Review of Anthropology 33. 21–45. Everett, Daniel. 2005. Cultural constraints on grammar and cognition in Pirahã. Current Anthropology 46(4). 621–646. Extra, Guus & Kutlay Yagmur. 2004. Urban multilingualism in Europe. Clevedon: Multilingual Matters. Fishman, Joshua A. 1982. Whorfianism of the third kind: ethnolinguistic diversity as a worldwide asset. Language in Society 11(1). 1–14. Fishman, Joshua A. 1991. Reversing language shift. Clevedon: Multilingual Matters. García, Olfelia. 2001. Language spread and its study in the twenty-first century. In Robert Kaplan (ed.), Oxford handbook of applied linguistics, 398–411. Oxford: Oxford University Press. Hajek, John. 2000. Towards a language history of East Timor. Quaderni del Dipartimeto di Linguistica, Universitá di Firenze 10. 213–222. Haugen, Einar. 1972. The ecology of language: essays by Einar Haugen. Stanford, CA: Stanford University Press. Halliday, M. A. K. 2001 [1990]. New ways of meaning: the challenge to applied linguistics. In Alwin Fill & Peter Mühlhäusler (eds.), The ecolinguistics reader, 175–202. London: Continuum. Harmon, David. 1996. Losing species, losing languages: connections between biological and linguistic diversity. Southwest Journal of Linguistics 15(10). 561–568. Heinrich, Patrick. 2012. The making of monolingual Japan: language ideology and Japanese modernity. Bristol: Multilingual Matters. Hornberger, Nancy H. 1998. Language policy, language education, language rights. Language in Society 27. 439–458. &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 S &6 308 2FWREHU30 165 A framework for language endangerment dynamics 1 Kaufman, Terrence. 1990. Language history in South America. In Doris L. Payne (ed.), Amazonian linguistics: studies in lowland South American languages, 13–67. Austin: 2 University of Texas Press. 3 Kulick, Don. 1992. Language shift and cultural reproduction. Cambridge: Cambridge University 4 Press. 5 Kymlicka, Will. 1995. Multicultural citizenship. Oxford: Oxford University Press. 6 Laycock, Donald. 2001 [1991]. Linguistic diversity in Melanesia. In Alwin Fill & Peter Mühlhäusler (eds.), The ecolinguistics reader, 167–174. London: Continuum. 7 8 Lupyan, Gary & Rick Dale. 2010. Language structure is partly determined by social structure. PloS One 5(1). 1–10. www.plosone.org (accessed 15 December 2011). 9 Mace, Ruth & Mark Pagel. 1995. A latitudinal gradient in the density of human languages in 10 North America. Proceedings of the Royal Society of London B. (Biological Sciences) 261. 11 117–121. 12 Marcellesi, Jean-Baptiste & Foued Larousie. 1997. France. In Hans Goebel, Peter H. Nelde, Zedenek Stary & Wolfgang Wölk (eds.), Kontaktlinguistik, Vol. II, Handbücher 13 zur Sprach-und Kommunikationswissenschaft, 1172–1187. Berlin & New York: de 14 Gruyter. 15 Marshall, Lorna. 1998. Sharing, talking, and giving. Relief of social tensions among the !Kung. 16 In John Gowdy (ed.), Limited wants, unlimited means. A reader in hunter-gather economics 17 and the environment, 65–85. Washington D.C.: Island Press. 18 Mufwene, Salikoko. 2008. Language evolution. London: Continuum. 19 Mühlhäusler, Peter. 1996. Linguistic ecology. Language change and linguistic imperialism in the Pacific Region. London: Routledge. 20 Mühlhäusler, Peter. 2000. Language planning and language ecology. Current Issues in 21 Language Planning 1(3). 306–367. 22 Mühlhäusler, Peter. 2005. Linguistic communities. In Fèlix Martí, Paul Ortega, Itziar Idiazabal, Andoni Barreña, Patxi Juaristi, Carme Junyent, Belen Uranga & Estibaliz Amorrortu (eds.), 23 Words in worlds: world languages review, 10–45. Clevedon: Multilingual Matters. 24 Nettle, Daniel. 1996. Language diversity in West Africa: an ecological approach. Journal of 25 Anthropological Archaeology 15. 403–438. 26 Nettle, David. 1999. Linguistic diversity. Oxford: Oxford University Press. 27 Nettle, David & Suzanne Romaine. 2000. Vanishing voices. Oxford: Oxford University Press. 28 Nichols, Johanna. 1997. Modeling ancient population structures and movement in linguistics. Annual Review of Anthropology 26. 359–384. 29 Ong, Walter J. 1982. Orality and literacy: the technologizing of the word. London: Methuen. 30 Ostler, Nicholas. 2005. Empires of the word. New York: HarperCollins. 31 Pantone, Dan James. 2008. Uncontacted Amazon Indians in Peru. http://www.amazon-indians. 32 org/Uncontacted-Amazon-Indians-Peru.html (accessed 10 December 2011). 33 Rhoter, Larry. 2005. Language born of colonialism thrives again in Amazon. New York Times. http://www.nytimes.com/2005/08/28/international/americas/28amazon. 34 html?pagewanted=all (accessed 10 December 2011). 35 Salminen, Tapani. 1997. Die gegenwärtige Lage der nordwestsibirischen Sprachen. Anachronia 36 4. 87–104. 37 Sampson, Geoffrey, David Gill & Peter Trudgill. 2009. Language complexity as an evolving 38 variable. Oxford: Oxford University Press. 39 Thurston, William R. 1987. Processes of change in the languages of North-Western New Britain. Canberra: Pacific Linguistics, Series B, No. 99. 40 &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 30 308LGS S 2FWREHU30 J. Wendel and P. Heinrich 166 Tönnies, Ferdinand. 2007 [1887]. Community and society. New Brunswick: Transaction Publishers. Trudgill, Peter. 2011. Sociolinguistic typology: social determinants of linguistic complexity. Oxford: Oxford University Press. UNESCO. 2003. Education in a multicultural world. Paris: UNESCO. Woodburn, James. 1998 [1981]. Egalitarian societies. In John Gowdy (ed.), Limited wants, unlimited means, 87–110. Washington D.C.: Island Press. Wray, Alison & Grace, George. 2007. The consequences of talking to strangers: evolutionary corollaries of socio-cultural influences on linguistic form. Lingua 117. 543–578. Wurm, Stephen A. 2002. Strategies for language maintenance and revival. In David Bradely & Maya Bradely (eds.), Language endangerment and language maintenance, 11–23. London: RoutledgeCurzon. Zent, Stanford. 2001. Acculturation and ethnobotanical knowledge loss among the Piaroa of Venezuela. In Luisa Maffi (ed.), On biocultural diversity: linking language, knowledge and the environment, 190–211. Washington D.C.: Smithsonian Institution Press. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 &6 :'*îPP '*0HWD6FLHQFH -,-6/ SS± BB 308LGS S 2FWREHU30
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