Road E–25 from 1960 to 2025 and its aggregate environmental impacts Babahoyo – Jujan case

Road E–25 from 1960 to 2025 and its aggregate environmental impacts Babahoyo – Jujan case

Authors

  • Guillermo Espin Guillermo Espin
  • Ildaura Espin

DOI:

https://doi.org/10.53591/iti.v18i25s1.3306

Keywords:

Environmental Impacts - Damages not accounted for in EIAs (Environmental Impact Assessments), which appear several years after the completion of the works. Habitat Bank - A bank created by financial institutions (UN, IDB, etc.) to subsidize and recognize these damages.

Abstract

Context: The Guayas River basin includes the Babahoyo River sub-basin, which originates in the canton of the same name and belongs to the province of Los Ríos. The city of Babahoyo has developed thanks to transportation infrastructure and investments in various sectors (roads, waterways, irrigation projects, urban expansion projects, the Babahoyo flood control project (GTZ, 1990), the bridge over the Guayas River, and an 11,000-hectare rice irrigation project). These development projects are state investments financed internationally, and they generate both positive and negative environmental impacts. These impacts are mitigated through environmental management plans. When additional impacts arise that are not addressed in these plans, they are called aggregate environmental impacts. To mitigate these, the Habitat Bank exists, which provides subsidies and acknowledges the damages incurred. The Habitat Bank was created by lending institutions, and these institutions are present in all lending countries, including the World Bank, CAF, IDB, and IMF, among others. Examples include Colombia, Brazil, and the United States. The socio-economic development of the Babahoyo canton encompasses roads, agriculture (rice/bananas), urban development, and agro-industry, among other sectors. Infrastructure development from 1965 to 2025 has included the construction of roads, urban expansion, agricultural projects, and more. This development has resulted in an additional environmental impact: flooding in areas ranging from 20,000 to 30,000 hectares. This situation did not occur before the 1960s. Objective: The objective of the habitat bank (in the world, created by the UN) is to subsidize the aggregate environmental damages created by the implementation of these development projects, for the aggregate impacts that were not considered by the environmental impact study; and also not in the management plan. Method: Environmental impacts follow the order of: Results: Vehicle Operation Costs – Negative: 10,000 hours x $10/hour x 60 days = $6.06; Agricultural Production Costs – Negative: $36 per sack = $72.06; Flora and Fauna Costs – Negative: 200.06 m³ x $0.06/m³ = $12.06; Infrastructure Costs – Negative: 20,000 vehicles x $1.75/hour x 60 days = $2.10; Damage to road infrastructure: $6.06 = $0.60; Damage to socio-economic infrastructure: 4,000 x 5 x 150 x 15.67 = $42.01; Aggregate impact per year (current value 2025) 6 + 72 + 12 + 2.1 + 0.6 + 42.01 = $134.71 E06. Conclusions: In ECUADOR there is no habitat bank, nor are there subsidies produced by the aggregate impacts of FLOODS THAT LAST 4 to 6 MONTHS PER YEAR, this impact creates socio-economic, psychosocial and environmental problems.

References

Asamblea Nacional del Ecuador. (2008). Constitución de la República del Ecuador. https://www.asambleanacional.gob.ec

Boardman, A. E., Greenberg, D. H., Vining, A. R., & Weimer, D. L. (2018). Cost-benefit analysis: Concepts and practice (5th ed.). Cambridge University Press.

CAF – Development Bank of Latin America. (2019). Environmental and social safeguards. https://www.caf.com

Canter, L. W. (1996). Environmental impact assessment (2nd ed.). McGraw-Hill.

CEQ – Council on Environmental Quality. (1997). Considering cumulative effects under the National Environmental Policy Act. https://ceq.doe.gov

Cooper, T. A., & Sheate, W. R. (2002). Cumulative effects assessment: A review of UK environmental impact statements. Environmental Impact Assessment Review, 22(4), 415–439.

Duinker, P. N., & Greig, L. A. (2006). The impotence of cumulative effects assessment in Canada. Environmental Management, 37(2), 153–161.

Forman, R. T. T., & Alexander, L. E. (1998). Roads and their major ecological effects. Annual Review of Ecology and Systematics, 29, 207–231.

Glasson, J., Therivel, R., & Chadwick, A. (2013). Introduction to environmental impact assessment (4th ed.). Routledge.

Instituto Geográfico Militar (IGM). (2020). Cartografía oficial del Ecuador. https://www.igm.gob.ec

Inter-American Development Bank (IDB). (2020). Environmental and social policy framework. https://www.iadb.org

IPCC. (2021). Climate change 2021: The physical science basis. Cambridge University Press. https://www.ipcc.ch

Ministerio del Ambiente, Agua y Transición Ecológica (MAATE). (2022). Política nacional del agua. Ecuador.

Ministerio de Transporte y Obras Públicas (MTOP). (2018). Normativa técnica para el diseño de carreteras. Ecuador.

Morgan, R. K. (2012). Environmental impact assessment: The state of the art. Impact Assessment and Project Appraisal, 30(1), 5–14. https://doi.org/10.1080/14615517.2012.661557

OECD. (2011). Environmental impacts of transport: Policy instruments and measures. OECD Publishing.

Pearce, D., Atkinson, G., & Mourato, S. (2006). Cost-benefit analysis and the environment: Recent developments. OECD Publishing.

UNESCO. (2023). United Nations world water development report 2023. https://unesdoc.unesco.org

World Bank. (2016). Environmental and social framework. https://www.worldbank.org

World Bank. (2020). Quality unknown: The invisible water crisis. https://openknowledge.worldbank.org

Downloads

Published

2026-06-30