Abstract

At an historic moment, when Colombia is emerging from 60 years of armed conflict, the 7-year-old Colombian Network for Ecological Restoration (Red Colombiana de Restauración Ecológica [REDCRE]) has created four subnational nodes, and is actively developing several more. All of this is taking place in the context of the Ibero-American and Caribbean Society for Ecological Restoration (Sociedad Ibero-Americana y del Caribe de la Restauración Ecológica [SIACRE]). In mid-November 2014, over 200 representatives of government agencies, academia, private enterprises, and nongovernmental organizations (NGOs) from the entire country attended a symposium to launch the Antioquia Province node, and take stock and plan the way forward. There are bright prospects of transdisciplinary and public–private collaborations in Colombia for ecological restoration and restoration of natural capital as part of a strategy to transition smoothly to a post-conflict era. We suggest some goals and guidelines to help move forward an ambitious agenda to mainstream ecological restoration.
NEWS ARTICLE
Toward a post-conict Colombia: restoring to the
future
Mauricio Aguilar1,2, Jorge Sierra3, Wilson Ramirez4, Orlando Vargas5, Zoraida Calle6,
William Vargas7, Carolina Murcia8,9, James Aronson10,11, José I. Barrera Cataño12
At an historic moment, when Colombia is emerging from 60 years of armed conict, the 7-year-old Colombian Network for
Ecological Restoration (Red Colombiana de Restauración Ecológica [REDCRE]) has created four subnational nodes, and is
actively developing several more. All of this is taking place in the context of the Ibero-American and Caribbean Society for
Ecological Restoration (Sociedad Ibero-Americana y del Caribe de la Restauración Ecológica [SIACRE]). In mid-November
2014, over 200 representatives of government agencies, academia, private enterprises, and nongovernmental organizations
(NGOs) from the entire country attended a symposium to launch the Antioquia Province node, and take stock and plan the
way forward. There are bright prospects of transdisciplinary and public private collaborations in Colombia for ecological
restoration and restoration of natural capital as part of a strategy to transition smoothly to a post-conict era. We suggest
some goals and guidelines to help move forward an ambitious agenda to mainstream ecological restoration.
Key words: networks, public private partnerships, REDCRE, SIACRE, subnational nodes
Introduction
After 60 years of internal armed conict, Colombia is poised
to enter a post-conict era in which ecological restoration could
play a signicant role. The recovery from such extended inter-
nal unrest requires signicant investment in the environment.
At least 40% of the continental territory is degraded (Etter et al.
2008), and current rates of deforestation are close to 273,000
ha/year (IDEAM 2010). Furthermore, the quality and quantity
of ecosystem services have been seriously impaired, as well as
the social capital and relationships between communities and
natural ecosystems (Murcia et al. 2013). In this context, eco-
logical restoration emerges as a self-evident means of restoring
natural and social capital and leveraging change across social
and political spectra. Indeed, Colombia has 50 years of practi-
cal experience in the ecological restoration of a wide range of
ecosystems (Murcia & Guariguata 2014). Grassroots network-
ing at national and international levels can be a highly useful
lever as well, provided government plays its role effectively.
However, for ecological restoration to be part of the strategy of
national recovery, it must be recognized and embraced in socioe-
conomic and political planning.
Recently, the Colombian government has undertaken var-
ious national and international engagements: in December
2012, it ratied the Hyderabad Call of the UN’s Convention
on Biological Diversity committing to the ambitious goal of
restoring 15% of all degraded ecosystems on Earth by 2020
(CBD 2012). Colombia also committed to full collaboration
with Objective 3(b)(i) of the Intergovernmental Platform on
Biodiversity and Ecosystem Services (IPBES 2013), which
calls for thematic assessments on degradation and restoration
of land and freshwater systems. It also supports the United
Nations Convention to Combat Desertication (UNCCD)’s new
policy to combat land degradation in a much more holistic
fashion, including large-scale ecosystem restoration (United
Nations Framework Convention on Climate Change 2012).
Recent policy includes the National Restoration Plan (Min-
isterio de Ambiente y Desarrollo Sostenible de Colombia
2012b), the 20102014 National Development Plan (DNP
2010), and the Manual for Assigning Compensatory Measures
(Ministerio de Ambiente y Desarrollo Sostenible de Colom-
bia 2012a), all of which include ecological restoration among
their goals, and a few state explicit goals in terms of physi-
cal area (hectares) and the amount of nancial resources to be
allocated.
Author contributions: MA, JS, WR, OV, ZC, WV, CM, JA, JIBC, conceived, wrote,
and edited the manuscript.
1Red Colombiana de Restauración (REDCRE), Instituto Alexander von Humboldt,
Bogotá, Colombia
2Address correspondence to M. Aguilar, email mauricioaguil@gmail.com
3Facultad de Ingeniería, Grupo de Estudios Florísticos, Universidad Católica de
Oriente, Rionegro, Colombia
4Biología de la Conservación, Instituto Alexander von Humboldt, Bogotá, Colombia
5Departamento de Biología, Universidad Nacional de Colombia, Bogotá, Colombia
6Restauración Ecológica, Fundación CIPAV, Cali, Colombia
7Restauración Ecológica, Corporación Paisajes Rurales, Cali, Colombia
8Department of Biology, University of Florida, Gainesville, FL 32611, U.S.A.
9Departamento de Ciencias Naturales y Matemáticas, Ponticia Universidad Javeriana
Seccional Cali, Cali, Colombia
10Center for Conservation and Sustainable Development, Missouri Botanical Garden,
St. Louis, MO 63166-0299, U.S.A.
11Restoration Group, Centre d’Écologie Fonctionnelle et Évolutive, Montpellier,
34293, France
12Departmento de Biología, Ponticia Universidad Javeriana, Bogotá, Colombia
© 2015 Society for Ecological Restoration
doi: 10.1111/rec.12172
4Restoration Ecology Vol. 23, No. 1, pp. 46 JANUARY 2015
Toward a post-conict Colombia
In this context, there is a clear need to undertake
capacity-building and networking in scientic, technical,
political, and social aspects of restoration, in order to respond
to the growing need and demand. Integration of ecological
restoration into landscape-scale planning, and restoration of
natural capital also needs to be encouraged and reinforced (see
Calle et al. 2012 for an example of this approach). Regard-
ing networking, there is much taking place throughout Latin
America. For example, in both Chile and México (Echeverria
et al. 2015), national networks of ecological restoration were
formed in 2014; Sociedad Iberoamericana y del Caribe de
Restauración Ecológica (SIACRE) will be hosting its 4th
International Conference in Buenos Aires, Argentina, in April
2015. In Colombia, the 7-year-old national network, Red
Colombiana de Restauración Ecológica (REDCRE), is estab-
lishing a series of subnational nodes, all interacting with local
communities, relevant institutions, NGOs, and the international
community devoted to the science and practice of ecological
restoration.
REDCRE’s mission is to generate opportunities for learning
and training, strengthening of existing know-how, and fostering
exchanges to promote greater synergy and collaboration in
the emerging eld of ecological restoration. Between 2007
and 2013, the core group of REDCRE in Bogotá created the
rst regional node, which offered and carried out formal and
informal courses at undergraduate and graduate levels, and
developed inter-institutional contracts between universities and
government agencies to undertake research, generate opera-
tional political and legislative tools, at national and subnational
levels, and raise awareness of the profound potential benets
of ecological restoration in ecological, cultural, and socioeco-
nomic spheres. Various practical manuals have been produced
for several types of Colombian ecosystems (e.g. Vargas 2007;
Barrera et al. 2010; Vargas 2011; Vargas et al. 2012), as well
as for a small but growing number of peer-reviewed articles
in national and international journals (Murcia & Guariguata
2014, and references therein). Additionally, two national sym-
posia and two congresses were held, and the 3rd International
Congress of SIACRE was hosted in Bogotá. REDCRE also
produces quarterly online bulletins describing the advances in
the science and practice of ecological restoration in Colombia.
Furthermore, the members of REDCRE provided support to
the Environment Ministry of Colombia, in the construction
and dissemination of the above-cited National Restoration
Plan.
REDCRE is now establishing subnational nodes to generate
technical capacity-building opportunities and optimize the
available human and nancial resource at provincial and local
levels. In 2012, a second subnational node was created in
Barranquilla, with a special focus on Caribbean, seasonally dry
tropical forests and coastal and marine ecosystems, including
mangroves and coral reefs. In early 2014, a third node was
created in the region known as Eje cafetero in Colombia, in the
middle Cauca valley. This node initially consisted of 16 people
and 8 institutions that together offer an online capacity-building
course for people in the region. In November 2014, a fourth
node was created in the Antioquia province, with headquarters
Figure 1. The organizers and some of the speakers at the inaugural
symposium of the Antioquia Node held in Rionegro, Colombia, 13– 14
November 2014.
in Rionegro. This group will concentrate on pre-montane and
montane forests, as well as on páramo. It is noteworthy that
Antioquia province has the most highly developed regional
economy in Colombia, with intensive and long-standing
activities in mining, agriculture, livestock production, and com-
mercial forestry. Concurrently, there is a considerable amount of
work on ecological restoration and rehabilitation, as well as on
ecological engineering. However, to date, those efforts have not
been well coordinated. Thus, the emergence of a well-organized
node in Antioquia, strongly integrated in REDCRE, is a timely
event.
At the inaugural event, in Rionegro, more than 220 people
from all over Colombia, with additional participants from
Ecuador, Mexico, and a representative-at-large of the SER
participated in a packed, 2-day program of fresh-from-the-eld
presentations of ongoing restoration work underway through
government agencies, corporate, NGO, and academics (Fig. 1).
In the closing discussion, 73 persons and 22 institutions pledged
their active involvement in the Antioquia node, and a rm com-
mitment was undertaken by all of them present to support the
rapid development of a nation-wide network of subnational
nodes.
Restoring to the Future
Six decades of armed conict, combined with cultivation of ille-
gal crops, have left the unintended consequence of reducing
development pressure on many regions (Alvarez 2003; Fjeldså
et al. 2005), allowing forest expansion of at least 3% in the last
decade (Sánchez-Cuervo et al. 2012). However, in the coming
post-conict era, massive deforestation could take place if the
government does not enforce the country’s strong environmen-
tal laws, and control the outcomes of ongoing negotiations for
forests and other ecosystems. Often, the argument is that the
JANUARY 2015 Restoration Ecology 5
Toward a post-conict Colombia
need to combat poverty and create jobs overrides environmen-
tal considerations. However, ecological restoration could be a
major and unifying theme and an important engine for job cre-
ation. We call on the people and government of Colombia to
leave behind the culture of conict and degradation that has
prevailed for half a century and work together toward a cul-
ture of conservation and restoration. There is already strong
and favorable policy in Colombia, but there must be much
stronger investments in capacity-building, at all levels from sec-
ondary schools to professional training, as well as integration
of ecological restoration in larger, landscape-scale, and biore-
gional efforts. Additional steps should include guidelines on
what researchers, NGOs, government agencies and the pub-
lic need to do to assure that in the next 510 years, there will
be a signicant shift toward mainstreaming ecological restora-
tion in society. REDCRE can also be very helpful in provid-
ing more substance to the National Plan for restoration, and
concerted effort to establish a national monitoring and eval-
uation effort (e.g. PACTO pela Restauração da Mata Atlân-
tica 2013), to track and evaluate ecological restoration success
and effectiveness on both ecological and socioeconomic goals
(Aronson et al. 2011).
Acknowledgments
The authors warmly thank J. Rubio (REDCRE), L. Chisacá
(SIACRE), Y. Betancur, and J. J. Garcia (UCO) for their excep-
tional technical support. They also thank REDCRE, UCO,
CORNARE, the Instituto Alexander von Humboldt, ISAGEN,
ECODES, CORANTIOQUIA, EPM, and SAG for their nan-
cial support of the Rionegro Symposium. They are also very
grateful to T. Mitchell Aide, an anonymous reviewer, and V.
Amaral for their constructive comments on a previous version
of the manuscript.
REFERENCES
Alvarez MD (2003) Forests in the time of violence: conservation implications of
the Colombian war. Journal of Sustainable Forestry 16:47– 68
Aronson J, Brancalion PHS, Durigan G, Rodrigues RR, Engel VL, Tabarelli M,
et al. (2011) What role should government regulation play in ecological
restoration? Ongoing debate in São Paulo State, Brazil. Restoration Ecol-
ogy 19:690– 695
Barrera JI, Contreras SM, Garzón NV, Moreno AC, Montoya SP (2010) Manual
para la restauración ecológica de los ecosistemas disturbados del Distrito
Capital. Secretaría Distrital de Ambiente, Bogotá, Colombia
Calle Z, Murgueitio E, Chará J (2012) Integrating forestry, sustainable
cattle-ranching and landscape restoration. Unasylva 63:31– 40
CBD (Convention of Biological Diversity) (2012) UNEP/CBD/COP Decision
XI/16. Ecosystem Restoration. http://www.cbd.int/doc/decisions/cop-11/
cop-11-dec-16-en.pdf (accessed 15 Nov 2014)
DNP (Departamento Nacional de Planeación) (2010) Plan Nacional de Desar-
rollo 2010– 2014, Prosperidad para Todos. https://www.dnp.gov.co/
PND/PND20102014.aspx (accessed 7 February 2013)
Echeverria C, Smith-Ramírez C, Aronson J, Barrera Cataño JI (2015) Good news
from Latin America. National and an international restoration networks are
moving ahead. Restoration Ecology 23:1– 3
Etter A, McAlpine C, Possingham H (2008) Historical patterns and drivers
of landscape change in Colombia since 1500: a regionalized spa-
tial approach. Annals of the Association of American Geographers
98:2– 23
Fjeldså J, Álvarez MD, Lazcano JM, León B (2005) Illicit crops and
armed conict as constraints on biodiversity conservation in the
Andes region. AMBIO: A Journal of the Human Environment 34:
205– 211
IDEAM (2010) Resumen ejecutivo de la memoria técnica de la cuanti-
cación de la deforestación histórica para Colombia, Bogota. Colombia.
https://www.siac.gov.co/documentos/DOC_Portal/DOC_Bosques/090311
_Articulo_deforestacion90_05.pdf (accessed 15 Nov 2014)
Intergovernmental Platform on Biodiversity and Ecosystem Services (2013)
Deliverable 3(b)(i): Thematic assessment on land degradation and restora-
tion. http://ipbes.net/work-programme/objective-3/45-work-programme/
459-deliverable-3bi.html (accessed 15 Nov 2014)
Ministerio de Ambiente y Desarrollo Sostenible de Colombia (2012a) Manual
para la Asignación de Compensaciones por Pérdida de Biodiversi-
dad. http://www.anla.gov.co/documentos/Manual_compensaciones.pdf
(accessed 16 Nov 2014)
Ministerio de Ambiente y Desarrollo Sostenible de Colombia (2012b)Plan
Nacional de Restauración: restauración ecológica, rehabilitación y
recuperación de áreas disturbadas. http://www.andi.com.co/Archivos/
le/Vicepresidencia%20Desarrollo%20Sostenible/PLANNACIONAL
RESTAURACION.pdf (accessed 16 Nov 2014)
Murcia C, Guariguata MR (2014) La restauración ecológica en Colombia:
tendencias, necesidades y oportunidades. Occasional Paper 107, CIFOR,
Bogor, Indonesia
Murcia C, Kattan GH, Andrade-Pérez GI (2013) Conserving biodiversity
in a complex biological and social setting: The case of Colombia.
Pages 86– 96. In: Sodhi NS, Gibson L, Raven PH (eds) Conservation
biology: voices from the tropics. John Wiley & Sons, Ltd., Hoboken,
New Jersey
PACTO pela Restauração da Mata Atlântica (2013) Protocolo de monitora-
mento para programas e projetos de restauração orestal. http://www.
pactomataatlantica.org.br/pdf/_protocolo_projetos_restauracao.pdf
(accessed 24 Nov 2014)
Sánchez-Cuervo AM, Aide TM, Clark ML, Etter A (2012) Land cover change in
Colombia: surprising forest recovery trends between 2001 and 2010. PLoS
One 7:e43943
United Nations Framework Convention on Climate Change (2012) Zero
Net Land Degradation, a Sustainable Development Goal for Rio20.
http://www.unccd.int/Lists/SiteDocumentLibrary/Rio+20/UNCCD_Policy
Brief_ZeroNetLandDegradation.pdf (accessed 15 Nov 2014)
Vargas O (2007) Page 194 Guía Metodológica para la Restauración Ecológica del
bosque altoandino. Universidad Nacional de Colombia, Bogotá, Colombia
Vargas O (2011) Los pasos fundamentales en la restauración ecológica. Pages
19– 40. In: Vargas O, Reyes SP (eds) La Restauración Ecológica en la Prác-
tica: memorias del I Congreso Colombiano de Restauración Ecológica y II
Simposio Nacional de Experiencias en Restauración Ecológica. Universi-
dad Nacional de Colombia, Bogotá
Vargas O, Díaz Triana JE, Reyes Bejarano SP, Gómez Ruiz PA (2012) Guías
técnicas para la restauración ecológica de los ecosistemas de Colombia,
Bogotá, Colombia. http://www.researchgate.net/publication/260365693_
Guas_tcnicas_para_la_restauracin_ecolgica_de_los_ecosistemas_de_
Colombia (accessed 17 Nov 2014)
Coordinating Editor: Valter Amaral Received: 17 November, 2014; First decision: 22 November, 2014; Revised: 26
November, 2014; Accepted: 26 November, 2014
6Restoration Ecology JANUARY 2015
... Protected areas have played an important role during the armed conflict [51]. The guerrillas, especially in the stages when the Colombian armed forces and paramilitary groups were at their strongest, found a refuge in the NNPs where they could continue their activities. ...
... The main goal in defining protected areas is to preserve environmental values and biodiversity [8], but, at the same time, it is also a priority to guarantee adequate development of the local populations [5,6,28,51]. This human development is linked to a compendium of cultural, environmental, social and biological factors that are often difficult to study separately. ...
... Thus, with the abandonment of guerrilla positions in some of the more isolated protected areas, key groups in land management (such as large landowners, peasants, cartels, etc.) seem to have expanded their activities in these areas, favouring large-scale livestock farming and speculative land markets or coca crops, with the resulting increase in deforestation and threats to biodiversity [46,53,73]. It is foreseeable that these activities have also had their effects on local population dynamics [51]. In this sense, if the effects of NNPs on local populations in situations of armed conflict remain to be explored, we have even less knowledge of the dynamics of post-conflict scenarios. ...
Article
Full-text available
It is widely recognised that conservation policies in protected areas must also favour the development and viability of human populations. Although much research has focused on economic consequences, understanding the real impact of conservation on local populations requires a more holistic standpoint. Using quasi-experimental matching methods and a diachronic perspective, the biodemographic and socio-economic effects of Colombia’s National Natural Parks (NNPs) were evaluated (all in a context of internal conflict and post-conflict). The analyses were made for the set of NNPs and then grouped into four natural regions (Andes, Caribbean, Amazon-Orinoquía and Pacific) and two conflict intensities. Differences were found mainly for NNPs with low-intensity conflict, but only for biodemographic variables, not for socio-economic ones. Starting from a situation of disadvantage, a relative improvement in the conditions of the NNP municipalities was observed throughout the 13-year period in relation to the control group. Results should be taken with caution due to the conflict situation, but the lack of correlation between biodemographic and socio-economic aspects highlights the need to include more complex approaches in protected area management policies
... To restore degraded lands, the national government announced in 2020 that 180 million trees would be planted by 2022 (Ministerio de Ambiente y Desarrollo Sostenible 2020). Colombia also committed to full collaboration with ambitious international initiatives such as the Intergovernmental Platform on Biodiversity and Ecosystem Services (IPBES), the United Nations Convention to Combat Desertification (UNCCD), and the UN's Convention on Biological Diversity (Aguilar et al. 2015). In this context, there is a critical need to assess the outcomes of forest restoration projects (McDonald et al. 2016;Gatica-Saavedra et al. 2017). ...
... In this sense, soil monitoring should consider innovation outputs for funding agencies, and give information that can represent direct economic benefits for landowners. Additionally, governments must strengthen their investments in capacity-building and increase financial incentives; especially in Colombia, this could be crucial to forest restoration policy implementation (Aguilar et al. 2015). All these issues would help to better incorporate soil monitoring in restoration practice, not only in Colombia, but also in other tropical or Latin-American countries, where soil monitoring has been somehow unaffordable. ...
Article
The knowledge of soil indicators during forest restoration is essential for understanding the recovery of ecosystem functions such as biomass production and water regulation. Despite this importance, in most restoration programs over the world, the soil remains under‐investigated. Here, we conducted a systematic literature review in order to determine: (i) the extent to which soil indicators are monitored during forest restoration in Colombia; (ii) the type of soil indicators (e.g., physical, chemical, or biological) that are used for the monitoring; and (iii) the regions where soil indicators are measured. We found 34 studies that report soil indicators. The most frequently studied restoration sites were 0–5 years old (36%). The majority (71%) of the studies only measured the soil characteristics at the topsoil. Soil sodium (Na) and phosphorus (P) concentrations were the most common chemical soil indicators reported by the studies. Soil biological indicators were the least frequently reported indicators. The studies rarely reported soil indicators that affect water movement directly. Of the retrieved studies, most included information about old‐growth forests (63%) or degraded sites (56%) for comparisons with forests undergoing restoration. Based on these results we provide recommendations for monitoring soil characteristics to assess the effectiveness of forest restoration projects in Colombia, and other tropical countries. This article is protected by copyright. All rights reserved.
... Fifthly, land use is defined as the formal or informal function of a certain land cover, 2 according to a given zoning plan or in disregard of it (van der Molen 2002). Although the impacts of conflicts on land use changes are understudied in literature (Garcia Corrales et al. 2019), there is evidence that conflict-driven migration, violence, and permanence of non-state actors may lead to the distortion of agricultural practices, such as the enforcement of illicit crops, the preference of seasonal instead of perennial crops (Arias et al. 2014), deforestation, and degradation (Aguilar et al. 2015). Lastly, as conflicts affect livelihood strategies by reducing financial, natural, and human capital, land-based capacity building, i.e., education support or vocational training, goes hand in hand with the reintegration of ex-combatants, the reversion of illicit agriculture, and rural development (Guarnieri 2003; Jaspars and O'Callaghan 2010; Subedi 2014). ...
Article
Full-text available
Conflicts have a strong impact on land tenure, use, distribution, accessibility, and governance; consequently, a sustainable strategy for peacebuilding requires the set-up of land-based institutional arrangements from the peace negotiation phase onwards. Based on the concept of territorial peace, these arrangements have a key role in the reconstruction of the collective, productive, and symbolic functions of the territory after conflicts, and in addressing conflict root causes related to land inequality. This paper contributes to the development of the concept of territorial peace by providing a framework for its operationalisation, based on three categories of arrangements, and testing it, to qualitatively explore and compare two comprehensive peace agreements: Colombia and the Philippines. Land may take the role of peacemaker in addressing territorial peace’s collective dimensions, especially when it is at the core of a peace agreement; however, its implementation remains volatile if it lacks trust, security, and technical capacity.
... In the last 50 years, native ecosystems in Colombia have been highly transformed by deforestation and land use change [29,30]. As result, the country has taken steps to restore degraded lands, for instance, Colombia's government recently adopted an ambitious 20-year National Restoration Plan and is actively participating in international restoration initiatives [31]. Nevertheless, restoration projects in Colombia rarely studied soil indicators and the hydrological services provided by tree planting are poorly understood [32]. ...
Article
Full-text available
Governments are increasingly committing to significant ecological restoration. However, the impacts of forest restoration on local hydrological services are surprisingly poorly understood. Particularly, limited information is available about the impacts of tree planting on soil infiltration processes and runoff pathways. Thus, we investigated the saturated hydraulic conductivity (Ks) and preferential flow pathways in three land-cover types: (i) Active Restoration, (ii) Degraded Land, and (iii) Reference Forest, with contrasting differences in soil profile and land use history in the municipality of La Jagua de Ibirico, César department, Colombia. We conducted soil sampling, using the Beerkan method to determine Ks values. We also measured vegetation attributes (i.e., canopy cover, vegetation height, diameter at breast height, and total number of trees) and carried out three dye tracer experiments for each study site. The blue dye experiments revealed that near surface matrix infiltration was dominant for Degraded Land, while at the Active Restoration and Reference Forest, this only occurred at local surface depressions. The general infiltration pattern at the three land uses is indicated as being macropore flow with mixed interaction with the matrix and highly affected by the presence of rock fragments. The deeper infiltration patterns occur by preferential flow due to the presence of roots and rock fragments. The mean Ks for the Active Restoration (240 mm h􀀀1) was much higher than the Ks at Degraded Land (40 mm h􀀀1) but still considerably lower than the Reference Forest (324 mm h􀀀1). These results indicate that top soil infiltration capacity and soil physical parameters not only directly regulate the amount of infiltration but also infiltration patterns and runoff processes, leading to lower infiltration and increased excess overland flow for Degraded Land than for other land uses.
... And these changes are linked to the new changes. types of political participation; Corruption negatively impacts economic development [35]. Injury is a problem that affects the social, political and economic activities of society [36]. ...
Article
Full-text available
Social and political instability threatens the economic and social development of nations. Political persecution is therefore characterized by socio-political instability as a barrier to development that creates economic difficulties, limited public and private investments and hinders national development. This article describes political persecution and economic development through a close examination of the African ministry which covers key issues such as welfare and drug trafficking. We use various measures to measure political violence and economic development, and we use the crisis management strategies of Driscoll and Kraay and a comprehensive time-based approach to measure (GMM) for a sample of Sub Saharan African countries in the period 2000-2014. In the example of political persecution, we find that the combination of individual achievement, education, capture, and health has a negative impact on politics, but GINI, unemployment, drugs and homeless people that have a positive impact on violence. In the example of the economy, political violence, armed with bribery and corruption, has a negative impact on economic development, but population, security, employment, political participation, housing have a negative impact on production and on economic progress. Positive impact on economic development. The findings underscore the importance of implementing social policies and guidelines against political violence to increase economic growth and development, productivity, political participation and human security in the regions of Africa.
... Restoration is mentioned in the Paris Agreement on climate change [94] [96]. Many countries are working toward integrating their restoration strategies into sustainable development and conservation agendas through national and subnational restoration plans and policies [97][98][99]. The UN REDD+ program is attempting to encourage the restoration of forests by creating a market value for the carbon stored in forests [100]. ...
... At the same time, natural resources can also be used as a tool for peace building and fostering cooperation(Le Billon 2000; Hatton et al. 2001;Conca and Wallace 2009). It is therefore well established that conflict and forest degradation are linked and conflict may facilitate or prevent largescale (e.g., industrial) exploitation of forests(Aguilar et al. 2015; Young and Goldman 2015;Bruch et al. 2016; Castro-Nunez et al. 2016a, b). ...
Chapter
Full-text available
Bonn Challenge is an ambitious global restoration pledge that was launched in 2011, with the nature-based solutions (NbS) strategy of forest landscape restoration (FLR) as its underlying principle. India has one of the largest pledges from Asia with the aim of bringing 13 million hectares of degraded land into restoration by the year 2020, and an additional eight million hectares by 2030, and thus should maintain a leadership position in South Asia on Bonn Challenge and landscape restoration. Government of India (GoI) and IUCN have prepared the first country progress report towards the Bonn Challenge pledge in 2018 which showed that India has already brought 9.8 million hectares into restoration. This report is the first progress report from any Bonn Challenge country and is also unique as it includes restoration efforts undertaken by the government, NGOs and the private sector. Although the government was the majority contributor (94.4%), the efforts of NGOs (3.6%) and private companies (2%) are important as they have the technical expertise to guarantee success. Three best practices of landscape restoration from across different ecosystems of India have been detailed here so that they may act as learnings for future restoration efforts. Lessons learnt from past restoration efforts have informed the design of a flagship project on FLR launched in five Indian States by GoI and IUCN, which will maintain India’s leadership on Bonn Challenge across South Asia.
... At the same time, natural resources can also be used as a tool for peace building and fostering cooperation(Le Billon 2000; Hatton et al. 2001;Conca and Wallace 2009). It is therefore well established that conflict and forest degradation are linked and conflict may facilitate or prevent largescale (e.g., industrial) exploitation of forests(Aguilar et al. 2015; Young and Goldman 2015;Bruch et al. 2016; Castro-Nunez et al. 2016a, b). ...
Chapter
Full-text available
Deforestation and forest degradation due to environmental change and anthropogenic pressure have resulted in significant reduction in the provision of valuable ecosystem goods and services. UNFCCC has emphasized forest conservation as a part of achieving sustainable development. These efforts have been reinforced through new global development agendas such as the Sustainable Development Goals (Goal 15) and the Aichi targets. A strong relationship between ecological restoration and the ecosystem services concept has been established, with the latter informing how ecological restoration may be planned and implemented. Deforestation and forest degradation in the Himalaya are a major concern. This region provides ecosystem goods and services to both upstream and downstream populations. International and national agencies and NGOs have been responding to the challenges of forest and environmental degradation through various planning activities and technologies. However, ecological restoration and rehabilitation of forests and degraded lands is the only viable strategy in the Himalaya to improve the environment, mitigate climate change impacts and support the livelihoods of natural resource dependent traditional communities. Large-scale failure of past efforts can be attributed by lack of a participatory strategy to determine the essential needs of the local population and gain their cooperation. GBP-NIHE has been active in the Indian Himalayan Region for over 25 years, significantly contributing to environmental conservation and sustainability, developing restoration models involving local people. This chapter describes ecological restoration undertaken by the Institute in the wasteland across the Indian Himalayan Region (IHR), to promote effective biodiversity conservation and sustainable development.
Preprint
Full-text available
Colombia is a notorious biodiversity hotspot that came to the spotlight of conservation upon the signing of the peace agreement in 2016. Here we used a counterfactual approach to forecast by 2036 the impact of deforestation on Colombia’s biodiversity and carbon stocks under three scenarios: (1) pre-signing of the peace agreement, (2) post-signing and (3) business-as-usual. We found that if deforestation rates continued at the same pace of post-signing, up to 41,000 km ² of forest area may be lost by 2036, whereas pre-signing rates would save nearly 25,000 km ² (equivalent to the total forest loss observed between 2000 and 2018). Under the pre-signing scenario, between 2018-2036 Colombia would reduce the average impact on the range of forest-specific species by nearly 50% of habitat area relative to 2000-2018, whereas under the post-signing scenario, it would increase by 33%. Moreover, losses of 312-807 Mm ³ of growing stock volume and 267-688 Mt of aboveground biomass were projected by 2036, jeopardizing the country’s commitments towards international conservation as well as climate targets. Importantly, we found a mismatch at the department level on biodiversity and biomass losses, which highlight an urgent need to generate coherent policies at a national level aiming to tackle both issues.
Book
Full-text available
En el libro SUCESIÓN ECOLÓGICA EN PAISAJES FRAGMENTADOS DE LA AMAZONIA COLOMBIANA se presentan los principales avances, en la generación de conocimiento, sobre la sucesión ecológica en los bosques secundarios, en áreas con alto grado de fragmentación en la Amazonia colombiana. A partir de dicho conocimiento, se muestran los diseños y las consideraciones técnicas y sociales para la implementación de acciones de restauración ecológica. La síntesis aquí presentada es una fuente de información académica para la formación de recurso humano y es el punto de partida para investigaciones futuras en torno a la sucesión ecológica, en bosques secundarios y su restauración. Adicionalmente, se constituye en una oferta tecnológica relevante para la Amazonia nor-occidental, para el desarrollo de procesos de restauración ecológica de las áreas de pasturas degradadas por uso ganadero y las áreas de protección de fuentes hídricas y humedales, consideradas como los ecosistemas más impactados en la intervención agropecuaria de la Amazonia y de mayor vulnerabilidad ante los efectos del cambio climático. Los resultados contenidos en esta publicación se obtuvieron en desarrollo del proyecto de investigación “Restauración de Áreas Disturbadas por Implementación de Sistemas Productivos Agropecuarios en zonas de Alta Intervención en el Caquetá “ejecutado mediante el Convenio No. 60-2013 suscrito entre la Gobernación del Caquetá y el Instituto Amazónicode Investigaciones Científicas SINCHI; co-ejecutado con la Universidad dela Amazonia, la Asociación de Reforestadores y Cultivadores de Caucho de Caquetá, (Asoheca) y la Federación Departamental de Ganaderos del Caquetá, (Fedeganga); cofinanciado con recursos del Fondo de Ciencia, Tecnología e Innovación - FCTeI del Sistema General de Regalías – SGR
Article
Full-text available
The livestock sector occupies about 30 percent of the land surface of the planet through grazing and feed-crop production. It is a leading driver of deforestation, land degradation, pollution, climate change, the sedimentation of coastal areas and invasions by alien species. Despite its inefficiency and its multiple negative effects on the environment, cattle ranching is not likely to decline any time soon in Latin America. First, this activity is deeply rooted in the Portuguese and Spanish ancestry of the region. The inputs of naturally intensive systems are biological processes rather than fossil fuels and synthetic compounds, and they apply modern scientific knowledge to combine and manage species with different traits. ISPSs respond to the increasingly urgent need to transform tropical cattle-ranching into an environmentally friendly activity that can be profitable in the short and medium terms and capable of generating more and better rural jobs while providing safe, high-quality food, hides and wood.
Chapter
Full-text available
The multi‐temporal and spatial scale interaction of history, geography, and evolution are responsible for Colombia's extreme diversity. This chapter first describe Colombia's biological complexity and its conservation context. Then, it presents some of the main challenges for conservation professionals, managers, and decision makers in their aim to preserve Colombia's rich biodiversity for generations to come. These challenges for biodiversity conservation in Colombia are divided into two categories: (1) territorial issues and current development models; and (2) threats specific to the different ecoregions. In addition, the challenges associated with conservation strategies, specifically the creation and management of protected areas (PAs) and ecological restoration are discussed.
Article
Full-text available
Degradation of ecosystems is ongoing in Latin America but there is also a strong upswing in conservation and restoration efforts. SIACRE – the Ibero-American and Caribbean Society for Ecological Restoration – is playing a key role in coordinating and promoting this trend at international, national, and subnational levels. In October 2014, SIACRE members organized the first national seminar on ecological restoration in Chile, with participants representing both academic and non-academic sectors. This seminar served as the catalyst for this essay and was an historic event at the national level. Much work has been underway in the science and practice of restoration in Chile, but until now it has been fragmented. This first national seminar enabled helped the principal strengths and challenges that Chile has and must face in the transdisciplinary domain of ecological restoration. Since 2004, various meetings have been organized in the region, in order to communicate the importance of restoration, especially in Mexico, Cuba, Colombia, Brazil, and more recently in Chile and Argentina. Here we trace the history of national and subnational restoration networks in Latin America and the Caribbean, and of SIACRE, and then outline some goals and challenges for the coming years.
Article
Full-text available
Forest remnants in the Colombian Amazon, Andes, and Choco are the last repositories of a highly diverse and endemic biota. Historical changes in the Colombian landscape have been dramatic, but the magnitude and rate of change has increased over the last half century, while conflict has consumed the capacity of Colombian society to respond to environmental threats. Academic experts in the study of the Colombian conflict have explored the social, political, and economic implications of the war. However, the environmental consequences of conflict are documented only when groups in conflict target salient economic resources. This paper presents the first analysis of the geographic distribution of forest remnants in relation to armed conflict in Colombia. Results show that guerrillas and/or paramilitaries range throughout areas of human encroachment into remnant forests. The policies promoted by Colombia's irregular armed forces range from "gunpoint conservation" rarely applied by guerrillas, to the rapid conversion of forests and crops to cattle ranches and coca (Erythroxylum sp.) plantations, following paramilitary occupation. Because the rates and extent of fragmentation are linked to such land use practices, armed groups may play a crucial role in determining the fate of Colombia's forests and their endemic biota.
Article
Full-text available
Background Monitoring land change at multiple spatial scales is essential for identifying hotspots of change, and for developing and implementing policies for conserving biodiversity and habitats. In the high diversity country of Colombia, these types of analyses are difficult because there is no consistent wall-to-wall, multi-temporal dataset for land-use and land-cover change. Methodology/Principal Findings To address this problem, we mapped annual land-use and land-cover from 2001 to 2010 in Colombia using MODIS (250 m) products coupled with reference data from high spatial resolution imagery (QuickBird) in Google Earth. We used QuickBird imagery to visually interpret percent cover of eight land cover classes used for classifier training and accuracy assessment. Based on these maps we evaluated land cover change at four spatial scales country, biome, ecoregion, and municipality. Of the 1,117 municipalities, 820 had a net gain in woody vegetation (28,092 km2) while 264 had a net loss (11,129 km2), which resulted in a net gain of 16,963 km2 in woody vegetation at the national scale. Woody regrowth mainly occurred in areas previously classified as mixed woody/plantation rather than agriculture/herbaceous. The majority of this gain occurred in the Moist Forest biome, within the montane forest ecoregions, while the greatest loss of woody vegetation occurred in the Llanos and Apure-Villavicencio ecoregions. Conclusions The unexpected forest recovery trend, particularly in the Andes, provides an opportunity to expand current protected areas and to promote habitat connectivity. Furthermore, ecoregions with intense land conversion (e.g. Northern Andean Páramo) and ecoregions under-represented in the protected area network (e.g. Llanos, Apure-Villavicencio Dry forest, and Magdalena-Urabá Moist forest ecoregions) should be considered for new protected areas.
Article
Full-text available
Around the world, there is growing desire and momentum for ecological restoration to happen faster, with better quality, and in more extensive areas. The question we ask is how can laws and governmental regulations best contribute to effective, successful, and broad-scale restoration? In the state of São Paulo, Brazil, there is a legal instrument (SMA 08-2008) whose aim is to increase the effectiveness of tropical forest restoration projects in particular. It establishes, among other things, requirements regarding the minimum number of native tree species to be reached within a given period of time in restoration projects and the precise proportion of functional groups or threatened species to be included when reforestation with native species is used as a restoration technique. There are, however, two differing perspectives among Brazilian restoration ecologists on the appropriateness of such detailed legal rules. For some, the rules help increase the chances that mandatory projects of ecological restoration will succeed. For the other group, there is no single way to achieve effective ecosystem restoration, and the existing science and know-how are far from sufficient to establish standardized technical and methodological norms or to justify that such norms be imposed. Both points of view are discussed here, aiming to help those developing new legislation and improving existing laws about ecological restoration. The precedents established in São Paulo, and at the federal level in Brazil, and the ongoing debate about those laws are worth considering and possibly applying elsewhere.
Article
Full-text available
The extent and the spatial patterns of landscape transformation we observe today are the result of the historic human settlement process, often dating back hundreds or thousands of years. Analyzing and reconstructing those historical patterns helps to advance the understanding of the dynamics and persistence of present-day ecosystems. This article explores this reconstruction by identifying and analyzing historic drivers of landscape change for seven periods between 1500 and 2000, and presents historical land use maps showing major trends and impacts on natural ecosystems. Historic land use maps were built using an ecosystem map of 1998 and a “preclearing” ecosystem map, by constraining the spatial change of transformed areas using data on accessibility to rivers and roads, elevation, slope, moisture availability, and settlement areas. We estimate the transformed area rose from approximately 15 Mha in 1500 to 42 Mha in 2000, and land use changed from cropping in 1500 to predominantly grazing in 2000. Demographic impacts of colonization and the introduction of cattle were major drivers of change, but rates and trends of land cover change varied between regions and from period to period. The most impacted ecosystems have been the Andean and tropical dry forests, with the most recent trends toward clearing of humid lowland forests, especially in the Amazon and Pacific. Some landscapes have been subject to strong human influence continuously for more than 500 years, whereas others have been transformed for less than thirty years. We discuss the relevance of a historical approach for guiding conservation goals, ecological restoration efforts, and research hypotheses.
Article
Full-text available
Coca, once grown for local consumption in the Andes, is now produced for external markets, often in areas with armed conflict. Internationally financed eradication campaigns force traffickers and growers to constantly relocate, making drug-related activities a principal cause of forest loss. The impact on biodiversity is known only in general terms, and this article presents the first regional analysis to identify areas of special concern, using bird data as proxy. The aim of conserving all species may be significantly constrained in the Santa Marta and Perijá mountains, Darién, some parts of the Central Andes in Colombia, and between the middle Marañón and middle Huallaga valleys in Peru. Solutions to the problem must address the root causes: international drug markets, long-lasting armed conflict, and lack of alternative income for the rural poor.