“Paiche reigns!” species introduction and indigenous fisheries in the Bolivian Amazon
© Macnaughton et al. 2015
Received: 14 April 2014
Accepted: 25 May 2015
Published: 30 June 2015
Species introduction, combined with changing access rules, increasing demand, and new road and dam infrastructure, are contributing to remarkable changes in Bolivian Amazon fisheries. This paper examines community responses to the appearance of a commercially valuable introduced fish species, Arapaima cf. gigas (“paiche”) in the Bolivian Amazon. Until the end of the 20th century, fisheries in this region were relatively low intensity, focused in rivers on a small number of native large-sized species by an urban-based commercial fishing fleet, and in floodplain lakes on a high diversity of native medium-sized species for subsistence by rural indigenous communities. In the seventies, Arapaima cf. gigas was introduced from Peru and has since invaded a significant portion of the Madre de Dios and Beni basins in northern Bolivia. This species now represents up to 80 % of commercial catches for the region. Occupying primarily floodplain lakes, many of which are located within indigenous territories, it has created economic opportunities and stimulated conflicts. The evolution of fisheries in one indigenous Tacana community is described, and the perspectives of local fishers are explored. Results suggest that while the new resource has strengthened incipient community-level organization, the current capture strategies and management mechanisms may not be conducive to sustainability or equitable distribution of returns. Commercial fisheries targeting a set of native species have been replaced by a single-species fishery in this community, raising questions about how the changes both in the resource-base and associated livelihood strategies are impacting system resilience. Ecosystem impacts of the introduction remain unclear. Paiche is viewed both as a potential threat and an opportunity by indigenous fishers. The management of this introduced species for a maximum social benefit and minimal environmental damage are topical concerns for communities and government actors and should be treated carefully considering local and broader, regional-scale implications.
KeywordsArtisanal fisheries Bolivian Amazon Introduced species Arapaima cf.gigas Adaptation Resilience
Globally, fisheries are increasingly vulnerable to a multitude of threats, resulting in an interest in fostering adaptation among fishing peoples (FAO 2007; Daw et al. 2009). Introduced species are considered one of the prime factors that contribute to the decline of native species and significant negative impacts on fishery-related livelihoods globally (Clavero and García-Berthou 2005; Shackleton et al. 2007). However, where communities have been able to make use of non-native aquatic species, these can sometimes also present a new, economically valuable resource, as is the case of a variety of introduced fish species in the reservoirs and rivers of south-central Brazil (Hoeinghaus et al. 2009), and the Nile perch in Lake Victoria (Mkumbo and Marshall 2015). The Nile perch, in particular, has supported remarkable economic development in central African lakes after its introduction in the late 1970s (Mkumbo and Marshall 2015), though its negative environmental impacts and inequitable social benefits have long been criticized (see for example Von Kaufmann 2007; Balirwa et al. 2003). This paper presents a case where introduced species are providing economic opportunity, and explores adaptation strategies and resilience capacity by local fishers.
Resilience and adaptation are key concepts in understanding and addressing the challenges that introduced species present to small-scale fisheries. The resilience concept (Holling 1973) describes a cycle whereby ecosystems, human systems (communities) and management systems absorb unexpected shocks and perturbations without collapsing or otherwise entering an intrinsically undesirable state (Berkes and Folke 1998). In other words, resilience is the capacity of a whole system to respond to disturbance and shocks, while maintaining essential functions (Walker et al. 2004; Folke et al. 2005; Folke 2006). In a fishery, resilience is pertinent for management institutions, fishing communities, value chain, and the ecosystem in which the fish live (Charles 2005). There is a growing interest in enhancing the resilience in fisheries (Allison et al. 2007). In this context, adaptation is based primarily on groups managing the fisheries resource system by intentionally or unintentionally moving thresholds within the system (Walker et al. 2004). In the case of species introduction, adaptation in fisheries includes not only thresholds related to the relationship between resource users and resources in an existing and potentially ‘knowable’ system, but also new interactions and thresholds with unpredictable outcomes resulting from the external driver. It is important to consider the wide consequences of disturbances and adaptation to external drivers on fisher well-being and to better understand how these strategies are implemented and feed back into the resilience of fisheries as a social-ecological system (Coulthard 2012); these elements are critical to informing effective resource management planning.
Arapaima cf. gigas (paiche in the study area; pirarucú in Brazil; hereafter referred to as paiche in the text), the world`s largest scaled freshwater fish, is native to the middle and lower portions of the Amazon Basin, where it has been largely overfished, but is not native to the Bolivian Amazon. Paiche was introduced to the upper Amazon headwaters of Peru in the 1960s (Carvajal-Vallejos et al. 2011), and first appeared in the Bolivian fisheries approximately 20 years ago. Currently it dominates the commercial catch in the northern Amazon region of Bolivia overall (Coca Méndez et al. 2012). Knowledge to date on the biological and ecological impacts of paiche introduction is presented in Miranda-Chumacero et al. (2013). The contributions of paiche to indigenous fisheries varies significantly at the local, or community level, and is likely influenced by a number of factors including access to floodplain lakes where paiche is present and abundant, adequate technology (gear and knowledge), connectivity to markets, and the mix of livelihood activities. Overall, high species diversity continues to be a key feature, both for subsistence and more recent commercial fishing in indigenous communities in the region surrounding Trinidacito. In a recent study by Argote et al. (2014), a total of 67 species were recorded in the fisheries catch for seven indigenous communities (including the study community of Trinidacito) over a one-month period. Native species landings were dominated by Characiformes, Siluriformes, and Perciformes, with medium-sized catfish and piranhas of particular importance. It is not yet known if, or how, paiche affects the native fish communities in the region.
The paiche invasion is occurring in the context of a rapidly changing social environment of land reforms, increasing urban and rural populations and expanding road access in Bolivia’s northern Amazon region. These intersect with an increasing indigenous ownership, political decentralization, and a largely undocumented and unmanaged fishery. This complex context circumscribes the potential adaptation strategies and capacity for resilience displayed among fishing communities in the region. Indigenous groups have traditional access rights to natural resources, recently recognized by the national government, and a vested interest in their sustainable use. However, they face significant challenges in developing and implementing resource management strategies, including low technical and financial capacity and weak monitoring capacity. A better understanding of the range of social and biological impacts of the paiche introduction, and of local priorities and underlying values concerning aquatic resource exploitation and conservation, could provide useful insights as to how local fisheries have adapted to change, and inform appropriate development strategies.
This study presents some local views about the social and ecological impacts of paiche, and its role in fishery development of one community, including perspectives from some of the most successful paiche fishers in the region thus far. In explores how people in an indigenous community perceive and act in response to an external driver, in the context of changing governance frameworks at different scales, and identifies the factors which contribute to adaptation and resilience in the local fisheries system.
The northern portion of the Bolivian Amazon is an area of about 100,000 km2, and includes the departments of Pando, Beni (Vaca Diez province) and a portion of La Paz (Iturralde province). An estimated three-quarters of this is upland tropical forest (Ibisch et al. 2003), but over 16 eco-regions are reported (Paramo 2005). The rivers, headwaters of the Amazon Basin, are home to a high diversity of fish species (Carvajal-Vallejos et al. 2014), and are considered of high ecological significance (Ibisch et al. 2003).
Indigenous communities in the Bolivian Amazon are largely organized in Communal Territories of Indigenous People (locally “Tierras de Comunidades de Origen” or TCOs), mostly located in forested areas, often close to rivers or lakes, with limited access to regional urban centres by unimproved roads or fluvial transport. In the region, these territories cover over 6921 km2, with an estimated total population of 69,000 (Soria 2011). Livelihoods and subsistence are based on small-scale agriculture, fishing, hunting, and gathering of forest products, according to local availability of resources.
TCO TIM II is comprised of communities belonging to three distinct indigenous groups (Esse Ejja, Tacana, Cavineño). This study focuses on the Tacana community of Trinidacito, located close to the banks of the Madre de Dios River, in an upland location (Fig. 1). Trinidacito is notable for its productive and locally managed commercial paiche fishery. The nearest urban centre is Riberalta, a regional river port city at the confluence of the Madre de Dios and Beni Rivers. This is the location of regional fish markets and exporters to national and international markets, and at the same time is the national centre for processing and export of wild-harvested Brazil nuts (Bertholletia excelsa) - the main contributor to the regional economy.
Information was collected from published sources and reports on the general history of indigenous groups and fishing activity in the region. This was complemented by detailed interviews with people locally identified in Trinidacito as the oldest or most knowledgeable with respect to community and fishing history. Interviewees were selected by a combination of purposeful sampling of community and fishing leaders (direct observation), and an exponential, non-discriminative snowball method (Berg 1988); respondents were asked the question, “who are the most active and experienced fishers in the community?” A total of 16 men and one woman were interviewed between August 2011 and June 2013. In many cases, fishers’ wives also participated in and contributed to the interviews. Data were transcribed and organized using NVivo 10 software, according to key themes, historic timelines, consensus regarding events and perspectives, etc. Drawing on methods from human ecology, an adapted process of progressive contextualization (Vayda 1983) was used in the analysis of interview data to organize the story of fisheries participation, paiche introduction and the local responses. Findings were compared with data available from comparable studies in other parts of the Amazon Basin.
Rights to natural resources were historically concentrated in large rubber-tapping estates known as barracas, held by a very small group of elites (Garland and Silva-Santiesteban 2004; Pacheco 2003). Following the Second World War, the barracas underwent reorganization towards other extractive activities, notably Brazil nut harvesting (Cardona 2012). Beginning in the 1990s, decentralization of government, re-assignment of land rights, and establishment of indigenous territories (Indigenous Community Territories - TCOs) all contributed to the development of modern indigenous settlement and livelihoods in the region. Current fisheries result from the combination of both historically practiced traditional subsistence activity and new commercial opportunities.
The recognition of communal rights for exclusive access and traditional use of natural renewable resources located within the TCO territories was included in the national land reform of 1996 (Garland and Silva-Santiesteban 2004). However, the rules defining and permitting commercial activity and individual extractive activity within this framework are not clear. Specific regulations on natural resource exploitation and sustainable management at the level of the TCOs continue to evolve, including for fisheries, as their commercial potential is increasingly recognized. A new national fisheries law proposal, which involved a high level of consultation with fishers in its development, is currently pending approval and will provide additional clarity on resource access rules.
There is very little documentation for commercial fisheries in northern Bolivia prior to the 1980s, but fishing activity likely began to increase during the slow end (1970s–1990s) of the rubber industry (Cardona 2012). At this time, a variety of communities (indigenous and campesino) living on barracas abandoned them to create new settlements and pursue previously disallowed independent agro-extractive livelihoods (Henkemans 2001). More communities were located in proximity to urban centres and people increasingly participated in the regional market economy (Pacheco 2003). The remaining barraca estates continued to dominate the landscape, mainly through the Brazil-nut industry, and controlled access to fisheries in many of the lakes and smaller streams until well into the 1990s (Cardona 2012). Between 1980 to mid-1990s, the focus of commercial fisheries in the region was the larger-bodied catfish and other high-value fish in the main rivers, carried out mostly by small to medium sized boats (Van Damme et al. 2011). The floodplain lakes were used by local communities for subsistence, while commercial fishing was carried out by urban-based boats, as they travelled along the main rivers and fished opportunistically in accessible lakes to supplement their catch from the river. These boats also purchased fish from the communities or traded in exchange for supplies. A new network of river traders emerged as the barracas system of community supply stores declined and road access continued to be very limited (Henkemans 2001). These new changes likely contributed to the formation of habilito relationships in the community-based fisheries, in which intermediaries provide credit for operational costs of harvesting in return for exclusive right to market the fish catch. This continues as a dominant factor in most of the commercial fisheries in the region.
In general, the participation of indigenous fishers in commercial activity in this region was relatively limited in terms of overall production volume, increasing rapidly only in the past 10 years. Prior to the emergence of the paiche fishery, commercial fisheries in the region focused on the exploitation of a handful of large-sized species in rivers and lakes such as Colossoma macropomum (local name pacú), Pseudoplatystoma spp. (local name surubí) and Zungaro zungaro (local name chanana) (Van Damme et al. 2011).
Arapaima cf. gigas (paiche), a new resource
The regional fisheries picture changed dramatically from the 1990s onward, due in large part to new fisheries based on the introduced paiche, currently making up over 60 % of total landings (by weight) for the Riberalta region, 40 % of indigenous commercial landings in the region (Coca Méndez et al. 2012), and 82 % of landings in Trinidacito (Argote et al. 2014). Paiche may also represent a number of new threats to the native fish resources (Van Damme et al. 2014).
Until very recently, paiche meat was sold in the national urban fish markets only as fillets of surubí catfish; while texture, taste and appearance of the two fish are distinct, consumers are not well-informed and do not usually discriminate between these species (Van Damme, personal observation). For the past three years, it has begun to appear in upscale restaurants and is now sold in some fish markets as paiche. While the main markets are regional urban centres in Bolivia (La Paz, Santa Cruz, Riberalta, Cobija) significant amounts of paiche are also sold fresh or salted to intermediaries who export it illegally across the border from Guayaramerín to Brazilian markets (Coca Méndez et al. 2012) where it is highly valued.
Local actor perspectives in Trinidacito
Trinidacito is a Tacana community, established in the early 20th century as a barraca for rubber extraction. It was governed by a local boss who lived in the community. A variety of caciques (local people appointed to leadership and regulatory roles) directed and financed fisheries activities until the community became involved with the indigenous movement around the time of the regional indigenous census in the early 1990s. The community was included in the creation of the TCO TIM II, following the Instituto Nacional de Reforma Agragia (INRA) law in 1996. The community is approximately 90 years old, among the oldest modern settlements in Pando Department, with 350 residents from 73 families. The main livelihood activities include seasonal harvest of Brazil nuts (January–March), fishing, agriculture and occasional participation in gold mining activity on the Madre de Dios River (Ledezma, unpublished data 2011). The community has one health post, one school, and unpaved road access to Riberalta (since 2006–7), one cellphone communication tower, recent wells for potable water (2013), and several gas-powered generators that are used sporadically.
Compared to other communities in the study region, Trinidacito has a relatively long history of local participation in commercial fishing activity. According to interviews, the formation of the oxbow lake Lago Mentiroso, currently the main fishing location for the community (Argote et al. 2014) and one of the most productive lakes in the region (Carvajal-Vallejos, unpublished data), was accelerated with the help of human modification (channel-cutting) by crew from one of these commercial boats around 1925. Consequently, it continues to have relatively high connectivity to the main stem of the river, facilitating entry of boats and, as a result, emergence of conflicts. Participation in commercial fishing activity is reported to have begun approximately 50 years ago, with a low level of organization and uncontrolled access by outsiders. For two decades (1960–70s) there was sporadic, uncontrolled entry into local lakes for commercial fishing by fishers from Riberalta and nearby communities. At this time, the lake fishery was based on the native species, mostly pacú and pacupeba (Mylossoma spp.), and fish were sold to medium-sized commercial boats (two person crew, and holding capacity of up to 10 tonnes) that were frequently travelling on the Madre de Dios River, carrying supplies and product to and from the barracas, occasionally fishing in the river and lakes, or trading goods for fish from local residents. Several of the older fishers describe fishing in cooperation with urban-based partners or investors during this time. Hook and line was the gear most frequently used, those who could afford them also used gill nets (500–1000 m in length). Interviewees reported very high abundance of fish during this period (for example, catches of 90–100 pacú (8–10 kg size) per 300 m of gill net). Less commercially desirable fish, such as corvina (Plagioscion squamosissimus) for example, were used locally for subsistence or discarded as by-catch (to “not waste salt”). The price at this time was very low, at Bs. 2 per kg of salt-dried fish (roughly equivalent to US $0.10).
“Those outsiders, those fishermen, how do you call them, the ‘professionals’ from Riberalta, were always coming in and plundering us…Problems arrived to them with all of this. They were fined and all of those things…we would confront them and take all the material they had. To get it back, they had to pay us a fine.”
Paiche appeared around Trinidacito sometime in the late 1980s (reportedly seen in Lago Mentiroso as early as 1984) but was not commercially exploited until at least 1990 when a small group of outside fishers (possibly from Brazil) were observed catching and transporting the paiche fresh on ice. Within a few years (1992), a group of three local male fishers began catching paiche and selling it salt-dried to two buyers from Riberalta, for Bs. 2.50–3 per kg (US $ 0.67–US $ 0.81 at the time). Other buyers on the Brazilian border (Guayaramerín) subsequently began paying Bs. 5 per kg (US $ 1.35 at the time). At this time, paiche was in high demand and extremely over-exploited in Brazil.
Likely triggered by this demand and responding to a new national legislation for regularizing associations, the local fishing association was registered in 1994 as a working union, with 14 original members. This union grew to more than 40 active members, described as very well organized and effective at regulating the activity, collecting fees and distributing permits. An unprecedented increase in paiche fishing and an accompanying decline in the abundance of native species were observed. Paiche production peaked for several years; one younger male fisher who arrived in 2001 comments that at this time there were many more paiche in the lake, and more people in the fishery (as high as 60 active members).
“In the past there were norms…one had to have a license, permission to enter the lake. Because in these licenses it said even in which boat one would be fishing. How many kilos, with what material. These licenses were used for one entry for fishing, nothing more. A permit, as you could call it. If you wanted to go in again, you needed another permit…I authorized people and gave them the papers…and there was another paper where kilos were recorded…”
Overlapping with this time period and jurisdiction, the creation of the TCO TIM II reserve in the 2000s led to a new process of negotiating, whereby agreements for each of its 34 communities were made to guarantee their access to traditional resources and land. Within the framework of TCO regulations, Trinidacito secured exclusive rights to Lago Mentiroso, due to the history of use and existing agreement with Pando Department. Resulting from this, the royalty payment was to be transferred to the local community association (who would pay a portion to the TCO TIM II government) and a third fee, monthly membership dues for the fishing union (Bs. 10 or US $ 2.70 at that time) was also instituted, though there was a period of confusion regarding the payment of fees, and legitimacy of the different agencies to collect them.
“Nowadays people work without any documentation, no permits…Who authorizes the entry in the lake? In the past…the lake itself belonged to the community, but those who were doing the work of the fishery were unionized with all the appropriate documentation …this was done so no one outside the community could come in, so there was work for people from here. So no one pirated. Now…anyone can come in….”
In 2007, road access to the community was improved, enabling faster transport to Riberalta (2 h) and a change in the habilito dependence, and fostering independence. Several fishers purchased motorcycles, and began transporting fresh fish directly to Riberalta markets in search of a better price. However, due to the high costs of credit and supplies required for paiche fishing, this also included setting up new networks of habilito with Riberalta buyers. Some buyers arrived by car and fishers reported that the main vehicle bought and carried 400 to 450 kg of paiche per trip, on average 3 times per week. Local estimates place the total number of paiche fished at 70–80 fish weekly (1000–1500 kg/week) during the peak production time of March – April (the beginning of the fishing season, after the Brazil-nut harvest). By 2012, paiche was almost exclusively transported to Riberalta by motorcycle and sold fresh, directly to large-scale intermediaries. Women in Riberalta, employed by these intermediaries, process and package the meat into large filets before its shipment by air to national markets.
Currently, the entire commercial fishery in Trinidacito is directed to paiche, while other smaller-bodied native species are reported to be fished for family consumption only, as secondary income for food, clothing, etc. “to sustain the family through the year”. Brazil nut harvesting continues to be a more profitable economic activity overall, providing the bulk of family income, used for improving housing or purchasing transportation.
“The paiche reigns! I would like only that they close this side [of the lake], locking it up, wrapping it up for two years. So that the countless thousands of kilos of fish will come here again. I haven’t fished those thousands of kg anymore. Just me! And we were 40 fishermen. He who fished least, weekly, arrived with 300 kg salt-dried, imagine the decline. He who fished least. It was a fantasy!”
“Heavily, they have diminished, in the case of the pacú at least. Back then, we caught pacú without need of gillnets. We’d catch 10-12-15 pacus in the day, just with fruit. Now there aren’t any. Since the presence of the paiche. There are a lot of paiche!”
In addition to access issues, the unequal distribution of benefits from the paiche fishery is one of the main conflicts. Overall, there is some debate at the community level over what to do with paiche, since it is seen as a revenue generator for only a few people, even though it is a communal resource. Some suggest re-establishing payments to the community association and creating more widely beneficial value-added processing activities. The recently amended TCO regulation (2013) now permits commercial fishing activity for a subset of communities through their local associations. Prior to this, only forestry and harvesting of forest products (under community management plans) were permitted. Individual economic opportunities are still not clearly recognized within this framework.
Trinidacito is the only community within the TCO TIM II with established local norms regulating the fishing activity, including specific rules for the exploitation of paiche. These include mandatory membership in the commercial fishing union/association, mandatory participation in monthly meetings, reporting of catch data, payment of royalty fees (until recently), and observation of fishery closures. Fisheries closures are determined according to perceived best seasonal periods for paiche exploitation, in coordination with other extractive and agricultural activities. Restrictions on gear-type inhibit gillnet use, unless for communal harvests (native species) for social or ceremonial purpose. A system of fines and exclusion set by the community leaders is applied for non-compliance with the regulations. There is some indication of a rule allowing temporary closures when it is perceived that the catch levels are declining. There are no rules or social norms regarding minimum size, or fishing paiche during the reproductive phase.
“It is prohibitively [sic] prohibited, the use of gillnets. They aren’t allowed in the regulation…for the TCO. They are prohibited…everyone knows they are prohibited. Prohibitively! [sic].”
“No…it scares the fish, and the gillnets destroy everything. Even the cats fall in them! They pull up everything, even the anacondas!”
“It would be good to allow them to some degree, in a controlled manner, maybe twice a month or something.”
The reasons for not using gillnets include “fish learning to avoid capture” or being scared off, rather than potential over-exploitation. The clandestine use of gillnets is a secondary conflict which includes equipment robbery, from within the community and from outsiders, or ‘borrowing’ and leaving material somewhere else. Several fishers report having paiche gillnets stolen from their hidden storage locations close to the lake.
“Nowadays we don’t have norms, as you’d call them…there is no legislation… people are like this, some want them, others are not interested…. But we have [local] rules of course. For example, one has to obey the rules. One has to accept to be organized, to be an associate in order to fish. If there is a monthly membership fee, to pay it. One has to have permission…. One has to be affiliated and in good standing and accept all the conditions that are put in place by the internal rules… [The rules were made when] it was observed that rules were missing. But even rules don’t necessarily mean ‘responsibility’, as many people know, for example these fishermen and salt-dryers who catch corvina [less commercially important] and throw it away….because they don’t want to waste salt on it…”
“Well, the paiche, despite being an introduced species in the country of Bolivia, the paiche has come to bring us many sources of work to the communities and the fishermen who are also from outside. It is a very profitable source…It’s good…We have maintained it for years, by fishing in a sustainable way….with our more traditional materials from here….hooks and lines.”
“For me, paiche is good, that’s it…because you can even eat it, it’s good for selling, everything.”
“For me, it would be much better for there to be paiche. It’s what sustains, like I said. It never disappears completely, good fish, it can always be fished.”
Only two fishers indicated that paiche should be reduced or exterminated, to eliminate predation on the native species that are locally important for subsistence. However, these same two respondents are young, full-time professional paiche fishers, with limited experience fishing the native species, and could be looking for increased opportunity to fish paiche.
The introduced paiche has significantly impacted local resource and governance systems since its appearance in Bolivia, in particular for the indigenous community of Trinidacito. This research provides insights into adaptations to introduced species, which we describe as they relate to 3 focus areas: local organization in response to the external driver of paiche, its contribution to diversified livelihood strategies and implications for resource sustainability, and the influence of conflicts.
External drivers and local organization
The evolution of the local fishery management system in Trinidacito has had several stages, responding to triggers from external pressures (conflicts with outside fishers and new species), developing within a changing environment of regulatory authority, and grounded in both historical formal relationships and local practice. This corresponds to the release, re-organization and exploitation components of the “Holling cycle” (Walker et al. 2004). The local fishery evolution shows evidence of adaptation as the community self-organized and learned to make use of the new resource. The community is now strongly engaged in commercial fisheries exploitation, based almost exclusively on paiche, with some local management, though conservation or sustainability practices for this are less evident than economic ones. However, while signs of over-exploitation of the native pacú and pacupeba fishery were becoming apparent in Trinidacito in the 1990s, the paiche fishery was building, thus avoiding the phases of overt collapse and re-organization that could have been expected of the native fish fishery. The relatively large scale of the paiche exploitation and regulatory uncertainty after the collapse of the CDP and the creation of the TCO TIM II, triggered re-organization and a strengthened local union – primarily to secure continued exclusive community access to the resource, and regulate distribution of paiche fishing rights. Most recently, the new road access, a shift to fresh fish, and renewed uncertainty of upper level authority have created new value chains and possibly is triggering a new phase of institutional re-organization. Institutional experience at the community level, possibly building on the history and social learning of rigid organization from the rubber era, contributed considerably to the success of formal steps of organization. For example, interviewees in Trinidacito identified the lack of a local regulatory officer as a key factor contributing to deteriorating conditions. Overlapping jurisdictions and unclear authority of different governance actors during the transition to TCO governance also appear to be causes for local concern.
Livelihoods diversification, conservation and sustainability
The paiche introduction has provided Trinidacito an opportunity for livelihood diversification (to include a new species and fishery), which can be a resilience-building mechanism (Allison and Ellis 2001; Marschke and Berkes 2006). Indigenous fisheries of the TCO TIM II in the Northern Bolivian Amazon are part of a multi-faceted livelihood that has evolved from a history of subsistence hunting and gathering to include more income-generating, commercial extractive activities including rubber, Brazil nuts, and most recently, fishing. This ability to diversify and adapt to resource availability is an important part of resilience in the face of multiple stressors. Livelihoods continue to be based on seasonal cycles of agriculture and Brazil nut harvest, with fisheries for subsistence and commerce playing an increasingly important role for many communities, though in general considered of a secondary supportive role. In some cases, such as Trinidacito, commercial fisheries have increased because of the availability and profitability of the paiche fishery, but continue to be practised as a seasonal activity, interspersed with Brazil nut harvesting, and still considered a secondary source of income, which may enable more flexibility and ability for small adjustments - for example to lower fishing effort when scarcity becomes apparent. This contrasts significantly with other fishing communities in the same reserve who do not have access to the same mix of livelihood activities as Trinidacito, and have a lower abundance of paiche in their lakes. For example, in the more recently settled, flood-vulnerable communities of El Sur (located near the Beni River, TCO TIM II) landings include a diversity of medium-bodied native species and significantly less paiche. Most community members are engaged in commercial fishing year-round, with fishing constituting a ‘safety-net’ to deal with other shocks of life on the floodplain. Fishing as a ‘buffer’ is an adaptation mechanism, which these communities utilize to increase their resilience to external stressors. This is also consistent with results from the Peruvian Amazon (see Coomes et al. 2010) and the observation of highly heterogeneous fisheries in small communities of the Brazilian Amazon (Castello et al. 2013).
The current Trinidacito model is an interesting example of a single-species commercial fishery, despite high diversity of native species in the region. Currently, there is clear evidence that Trinidacito fishers are targeting paiche exclusively for their commercial fishery, with occasional opportunistic capture of other species for subsistence or sometimes for sale. This represents a significant shift in their fishery, and its implications for fishing effort, resource sustainability, or long term resilience are not clear. There is insufficient data available to determine the abundance of the native fish species in the lagoons surrounding Trinidacito and whether this has been affected by the paiche or fishing pressure.
Significant changes are evident in biological and social aspects of the fishery, demonstrating social innovation and adaptation, as well as a mismatch between expressed conservation interests and a lack of evidence of accompanying stewardship behaviours. The catch composition in the overall region has shifted considerably; fishing effort in Trinidacito is almost exclusively dedicated to paiche harvest. While local knowledge of the autochthonous species and interest in conservation were evident, these were not connected with associated stewardship behaviours to protect threatened stocks. For example, serious reductions of fish stocks of pacú, pacupeba, and paiche were referred to, though these are not evident from the sparse fishing data. Perception on the cause of these reductions was not clear, though local overfishing is considered a very likely factor. Interviewees also expressed concern about overfishing and waste (such as discarded by-catch for species such as corvina), and are asking for more restrictive management, both for sustainability and to reduce waste, but are not necessarily practicing conservation in their fishing methods.
Trinidacito is one of earliest indigenous communities to develop a commercial fishery in the region, initially responding to a strong market for native fish, facilitated by its proximity to the Madre de Dios river, the proximate location of a large, deep, productive floodplain lake (Lago Mentiroso), and increasing connectivity with regional markets in Riberalta. User conflicts have been exacerbated by the presence of this highly valued resource within indigenous territories; the unequal distribution of benefits from fisheries is an ongoing concern for all of the fisheries in the region. This included conflicts with outside fishers that triggered early self-organization and a lobby by the community to department-level authorities to gain exclusive community access to the resource. Two main persistent conflicts referred to in the interviews were those between local and outside fishers, and the relationship between the fishers and intermediaries (habilito).
The first of these, conflict over access, has triggered stronger levels of community organization that undoubtedly helped the development of the community overall, highlighting the potential positive spin-offs of conflict as a stimulus for change and improved resilience. Similar conflicts in other communities in the TCO TIM II did not appear to be so dramatic, and did not trigger similar levels of community organization.
The second source of conflict, habilito, a social contract in fisheries where credit is provided to fishers in exchange for exclusive right to the fish catch, is a dominant factor in most of the commercial fisheries in the region. This relationship is generally not favourable for the fishers, and is based on a long history of similar arrangements for extractive workers in this area for rubber, Brazil nut, and mining activities. In general, habilito enables a relative monopoly of some aspect of the value chain by the intermediary, for example transport, ice, or market access. To some extent, this element was challenged in Trinidacito with new road access and the profitability of paiche, which allowed fishers to transport their catch to urban markets directly by motorcycle and to experiment with the establishment of a local processing plant in the community. It remains to be seen if the new value chain links created through these changes are better than the earlier habilito system, or if new habilito arrangements will be created.
Introduced species may represent both new opportunities and challenges to fishing communities that influence their well-being and resilience. For example, the introduced Nile Perch in Lake Victoria constituted about 66 % of the total catch at its peak in 1990 (Mkumbo and Marshall 2015), but its introduction has been described as a socio-environmental failure from the perspective of impacts on local human communities (Von Kaufmann 2007), presumably with attendant reduced resilience. The paiche fishery in Bolivia, perhaps most advanced in Trinidacito, has shown some evolutionary steps reflecting the Holling cycles of resilience thinking (Holling 1973; Walker et al. 2004). These steps have been fostered by community cohesion, created through conflicts over access and the distribution of benefits, but tempered by historical social capital from the rubber-tapping era of both positive organizational capacity and fiscally-oriented monitoring mechanisms that vary in effectiveness. An evolving local organization adapting to a changing resource base and external pressures has been able to demonstrate strengths and deficits in expanding community-based fishery management and fisheries practices. While fishers maintain a diversified seasonal livelihood strategy, they have also increased single species exploitation instead of a traditional focus on small-bodied native species. While the fishery is still too young to assess how long-term resilience and well being will be affected by the introduction of paiche, information reported here will help inform multiple scales of regulatory and development strategies to foster positive outcomes for indigenous communities that may take advantage of the new opportunity paiche presents.
This study was carried out with the aid of a grant from the International Development Research Centre (IDRC), Ottawa, Canada, www.idrc.ca, and with financial support from the Government of Canada, provided through the Department of Foreign Affairs, Trade and Development (DFATD). The authors would like to thank CIDOB (Confederation of Indigenous Peoples of Bolivia), CIRABO (Regional Centre for Indigenous Peoples of the Bolivian Amazon), CIPOAP (Regional Centre for Indigenous Peoples of the Bolivian Amazon in Pando), the TCO TIM II (Indigenous Communal Territory Multi-ethnic Territory Two) directory and FEUPECOPINAB (Federation of Fishermen, Fish Sellers and Aquaculturists of the Bolivian North Amazon) for their collaboration and support of the research, and the Limnology and Aquatic Resources Laboratory at Mayor de San Simón University (ULRA-UMSS) for assistance in fish identification. We gratefully acknowledge F Machicao and G Rey for collecting fisheries data, C Coca and J Barrozo for conducting interviews, A Arteaga for field support, R Salas and E Herrera for key details of the local history, J Ledezma for information on the community, FB Davy, M Goetz and two anonymous reviewers for reviewing and contributing to the document, M Gasalla and the Maritime Studies Editorial Team for their editorial support. Finally, the authors would like to extend their gratitude to all of the fishers and their families in Trinidacito and the TCO TIM II, who generously offered their time and knowledge to make this study possible.
- Allison, EH, NL Andrew, and J Oliver. 2007. Enhancing the resilience of inland fisheries and aquaculture systems to climate change. Journal of Semi-Arid Tropical Agricultural Research 4(1): 35.Google Scholar
- Allison, EH, and F Ellis. 2001. The livelihoods approach and management of small-scale fisheries. Marine Policy 25: 377–388. doi:https://doi.org/10.1016/S0308-597X(01)00023-9.View ArticleGoogle Scholar
- Amaral, Benedito Domingues. 2005. Fisheries and fishing effort at the indigenous reserves Ashaninka/Kaxinawá, River Breu, Brazil/Peru. Acta Amazonica 35(2): 133–144. doi:https://doi.org/10.1590/S0044-59672005000200004.View ArticleGoogle Scholar
- Argote, Adalid, Paul A Van Damme, Alison E Macnaughton, and Fernando Carvajal-Vallejos. 2014. Pesca indígena en la amazonía boliviana: un caso de estudio en la Tierra Comunitaria de Origen Multiétnico II (Pando Y Beni). In Línea de Base Sobre Ecosistemas Y Recursos Acuáticos, ed. MRE-MMAyA. Cochabamba, Bolivia: Edit. INIA.Google Scholar
- Balirwa, John S, Colin A Chapman, and Lauren J Chapman. 2003. Biodiversity and fishery sustainability in the Lake Victoria Basin: an unexpected marriage? BioScience 53(8): 703–715.View ArticleGoogle Scholar
- Berg, S. 1988. Snowball sampling. In Encyclopaedia of Statistical Sciences, 8th ed, ed. S Kotz and NL Johnson, 529–532.Google Scholar
- Berkes, F, and C Folke. 1998. Linking social and ecological systems for resilience and sustainability. In Linking Social and Ecological Systems: Management Practices and Social Mechanisms for Building Resilience, ed. F Berkes and C Folke, 1–27. Cambridge: Cambridge University Press.Google Scholar
- Cardona, Walter C. 2012. Formal Institutions, Local Arrangements and Conflicts in Northern Bolivian Communities after Forest Governance Reforms. PROMAB Scientific Series 14. Riberalta, Bolivia: PROMAB.Google Scholar
- Carvajal-Vallejos, Fernando M., Rémy Bigorne, América J. Zeballos Fernández, Jaime Sarmiento, Soraya Barrera, Takayuki Yunoki, et al. 2014. Fish-AMAZBOL: A database on freshwater fishes of the Bolivian Amazon. Hydrobiologia, March. doi:https://doi.org/10.1007/s10750-014-1841-5.
- Carvajal-Vallejos, Fernando, Paul Van Damme, Leslie Cordova, and Claudia Coca Mendéz. 2011. La introducción de arapaima gigas (paiche) en la amazonía boliviana. In Los Peces y Delfines de la Amazonía Boliviana: Hábitats, Potencialidades y Amenazas, ed. Paul A Van Damme, Fernando M Carvajal-Vallejos, and Jorge Molina Carpio, 367–396. Cochabamba, Bolivia: Editora INIA.Google Scholar
- Castello, L. 2004. A method to count pirarucu arapaima gigas: fishers, assessment, and management. North American Journal of Fisheries Management 24: 379–389.View ArticleGoogle Scholar
- Castello, Leandro, David G McGrath, Caroline C Arantes, and Oriana T Almeida. 2013. Accounting for Heterogeneity in Small-Scale Fisheries Management: The Amazon Case. Marine Policy 38 557–65. doi:https://doi.org/10.1016/j.marpol.2012.09.001.
- Castello, Leandro, David G. McGrath, and Pieter S.a. Beck. 2011. Resource Sustainability in Small-Scale Fisheries in the Lower Amazon Floodplains. Fisheries Research. Elsevier B.V. 110(2):356–64. doi:https://doi.org/10.1016/j.fishres.2011.05.002.
- Charles, A. 2005. Toward sustainable and resilient fisheries: a fishery-system approach to overcoming the factors of unsustainability. In Overcoming Factors of Unsustainability and Overexploitation in Fisheries: Selected Papers on Issues and Approaches. FAO Fisheries Report, ed. J Swan and D Greboval, 221–233. Rome: FAO.Google Scholar
- Clavero, M., and E. García-Berthou. 2005. Invasive species are a leading cause of animal extinctions. TRENDS in Ecology and Evolution 20(3). http://18.104.22.168/bds-cbc/sites/default/files/TREE05.pdf
- Coca Méndez, Claudia, Gabriela Rico, M Fernando, Roxana Salas Carvajal-Vallejos, M John Wojchiechowski, A Paul, and John Van Damme. 2012. La Cadena de Valor del Pescado en el Norte Amazónico de Bolivia: la Contribución de Especies Nativas y de una Especie Introducida (el Paiche - Arapaima Gigas). La Paz, Bolivia: Embajada Real de Dinamarca, IDRC, Fundación PIEB.Google Scholar
- Coomes, OT, Y Takasaki, C Abizaid, and BL Barham. 2010. Floodplain fisheries as natural insurance for the rural poor in tropical forest environments: evidence from Amazonia. Fisheries Management and Ecology 17: 513–521.View ArticleGoogle Scholar
- Coulthard, S. 2012. Can we be both resilient and well, and what choices do people have? Incorporating agency into the resilience debate from a fisheries perspective. Ecology and Society 17(1): 4. doi:https://doi.org/10.5751/ES-04483-170104.View ArticleGoogle Scholar
- Daw, T, WN Adger, K Brown, and MC Badjeck. 2009. Climate change implications for fisheries and aquaculture: overview of current scientific knowledge. In Climate Change Implications for Fisheries and Aquaculture: Overview of Current Scientific Knowledge. FAO Fisheries and Aquaculture Technical Paper No. 530, ed. K Cochrane, C De Young, D Soto, and T Bahri, 107–150. Rome: FAO.Google Scholar
- Folke, C. 2006. Resilience: the emergence of a perspective for social-ecological systems analyses. Global Environmental Change 16(3):253–267. doi:https://doi.org/10.1016/j.gloenvcha.2006.04.002.View ArticleGoogle Scholar
- Folke, Carl, Thomas Hahn, Per Olsson, and Jon Norberg. 2005. Adaptive governance of social-ecological systems. Annual Review of Environment and Resources 30(1):441–473. doi:https://doi.org/10.1146/annurev.energy.30.050504.144511.View ArticleGoogle Scholar
- Food and Agricultural Organization of the United Nations (FAO). 2007. Building adaptive capacity to climate change. Policies to Sustain Livelihoods and Fisheries. New Directions in Fisheries. A Series of Policy Briefs on Development Issues. No. 8. Rome: FAO.Google Scholar
- Garland, Eduardo B, and Alvaro B Silva-Santiesteban. 2004. Enganche y Servidumbre por Deudas en Bolivia. Working Paper 41. Geneva: International Labour Organization.Google Scholar
- Henkemans, Ariënne B. 2001. Tranquilidad and hardship in the forest: livelihoods and perceptions of camba forest dwellers in the northern Bolivian Amazon. Programa Manejo de Bosques de La Amazonia Boliviana PROMAB Scientific Series 5. Riberalta, Bolivia: PROMAB.Google Scholar
- Hoeinghaus, DJ, AA Agostinho, LC Gomes, FM Pelicice, EK Okada, JD Latini, EAL Kashiwaqui, and KO Winemiller. 2009. Effects of river impoundment on ecosystem services of large tropical rivers: embodied energy and market value of artisanal fisheries. Conservation Biology 23(5): 1222–1231.View ArticleGoogle Scholar
- Holling, CS. 1973. Resilience and stability of ecological systems. Annual Review of Ecology and Systematics 4: 1–23.View ArticleGoogle Scholar
- Ibisch, PL, JC Chive, SD Espinoza, and NV Araujo. 2003. Hacia un mapa del estado de conservación de los ecosistemas de Bolivia. In Biodiversidad: La Riqueza de Bolivia. Estado de Conocimiento Y Conservación, ed. P Ibisch and G Mérida, 264–272. Santa Cruz, Bolivia: Editora FAN.Google Scholar
- Imbiriba, EP. 1994. Reproducao, larvae e alevinagem de pirarucu (Arapaima Gigas). Belem, Brazil: Circular Tecnica 57.Google Scholar
- Marschke, MJ, and F Berkes. 2006. Exploring strategies that build livelihood resilience: a case from Cambodia. Ecology and Society 11(1): 42. www.ecologyandsociety.org/vol11/iss1/art42/.Google Scholar
- Miranda-Chumacero, Guido, Robert Wallace, Hailín Calderón, Gonzalo Calderón, Phil Willink, Marcelo Guerrero, Teddy Siles, Kantuta Lara, and Darío Chuqui. 2012. Distribution of Arapaima (Arapaima Gigas) (Pisces: Arapaimatidae) in Bolivia: Implications in the Control and Management of a Non-Native Population. BioInvasions Records. doi:https://doi.org/10.3391/bir.2012.1.2.09.
- Mkumbo, OC, and BE Marshall. 2015. The Nile Perch Fishery of Lake Victoria: Current Status and Management Challenges. Fisheries Management and Ecology 22: 56–63. doi:https://doi.org/10.1111/fme.12084.View ArticleGoogle Scholar
- Navarro, G, and Mabel Maldonado. 2005. Geografia Ecologica de Bolivia, Vegetacion Y Ambientes Acuaticos. La Paz, Bolivia: Fundacion Simon I Patio.Google Scholar
- Pacheco, P. 2003. Municipalidades y participación local en la gestión forestal en Bolivia. In Gestión Forestal Municipal En América Latina, ed. L Ferroukhi, 19–56. Bogor, Indonesia: CIFOR/IDRC.Google Scholar
- Paramo. 2005. Geografía de la Conservación de los Andes Tropicales: Bolivia, Colombia, Ecuador, Perú y Venezuela. http://www.paramo.org/node/1656
- Shackleton, CM, D McGarry, S Fourie, J Gambiza, SE Shackleton, and C Fabricius. 2007. Assessing the effects of invasive alien species on rural livelihoods: case examples and a framework from South Africa. Human Ecology 35(1): 113–127. http://www.jstor.org/stable/27654173.View ArticleGoogle Scholar
- Soria, GF. 2011. Territorios Indígena Originario Campesinos En Bolivia, Entre La Loma Santa Y La Pachamama. La Paz, Bolivia: Fundación Tierra.Google Scholar
- Van, Damme, A Paul, Fernando M Carvajal-Vallejos, Córdova Leslie, A Rua, and Becerra Pilar. 2011. Pesca comercial en la cuenca amazónica boliviana. In Los Peces y Delfines de la Amazonía Boliviana: Hábitats, Potencialidades y Amenazas, ed. Paul A Van Damme, Fernando M Carvajal-Vallejos, and Jorge Molina, 247–291. Cochabamba, Bolivia: Editora INIA.Google Scholar
- Van Damme, Paul A, Fernando M Carvajal-Vallejos, Marc Pouilly, Tamara Perez, and Jorge Molina Carpio. 2014. Amenazas para los peces y las pesquerías de la Amazonía Boliviana. In Los Peces y Delfines de la Amazonía Boliviana: Hábitats, Potencialidades y Amenazas, ed. Paul A Van Damme, Fernando M Carvajal-Vallejos, and Jorge Molina Carpio, 327–366. Cochabamba, Bolivia: Editora INIA.Google Scholar
- Vayda, Peter. 1983. Progressive Contextualization: Methods for Research in Human Ecology. Human Ecology 11(3): 265–281.View ArticleGoogle Scholar
- Von Kaufmann, KH. 2007. The Deathpond. Futures 39: 763–767.View ArticleGoogle Scholar
- Walker, B, CS Holling, SR Carpenter, and A Kinzig. 2004. Resilience, adaptability and transformability in social–ecological systems. Ecology and Society 9(2): 5. http://www.ecologyandsociety.org/vol9/iss2/art5/.
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