Application of Geospatial Techniques for Monitoring Gikondo Wetland Management: from Industrial Park to Eco-Tourism Park
Abstract
For several years, Gikondo Wetland has been serving as home for industries, warehouses, garages, and was critically degraded by various anthropogenic activities since its establishment as industrial parkin 1960s. The objective of this study is to analyse quantitatively and qualitatively the dynamics of Gikondo Wetland degradation and its rehabilitation progress from industrial to eco-tourism Park. Geo spatial techniques (GIS and Remote Sensing) have been used to analyse changes induced by management techniques from 1987 to 2019. Results show that wetland area has reduced from 32.03% (1987) up to 25.70% (2010) indicating its degradation due to the increase of built up areas and bareland over the wetland area. From 2010 to 2019, the area of wetland has increased. This positive change of land cover is indicating a good progress of Gikondo wetland restoration process. Continuing reinforcement of national legal framework is required and the implantation of development programs should be done with minimum tradeoffs in order to achieve the transformation of this former industrial park into an eco-tourism park. Rehabilitation process should consider wetland functions, services, and replacement options for achieving sustainable use and management of wetlands in Rwanda.
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Introduction
In 1950, only 30 % of the world’spopulation was urban. In 2018, the world’spopulation was residing in urban areas reached 55 % and the figure is estimated to be 68 percent by 2050 (UN, 2019). Cities and towns are continuingly becoming the primary human living space as countries develop. However, different studies highlight that accelerated urbanization is blamed to have negative impacts on urban environment especially on wetland ecosystems. This is due to fact that many world wetlands were taken as wastelands, difficult to use for agriculture or urbanization purposes. The above perspective has found place in Rwanda wetland management. Rural urban migration, high population growth, and provision of improved urban infrastructures such as roads and industries have contributed to increased urbanization by 26.70%. Moreover, lack of coordination between environment and urban planning sector has contributed to human occupation of wetland ecosystems especially in Kigali. Residential expansion, industrial and commercial activities have contributed to the loss or degradation of wetlands of Kigali city. Uncontrolled engineering activities have contributed much on destruction of wetland flora and fauna. In the same vein, the lack of effective wetland management strategies has resulted in the development of infrastructures such as roads and buildings within wetland area.
The case of Gikondo wetland has drawn the attention on the underperformance of industry and urban planning. This wetland, stretching from Gikondo to Nyabugogo was selected as industrial area since the independence. Therefore, it was greatly affected, and its ability to control siltation, and clean wastewater and buffer flooding was jeopardized[2]. The development of some infrastructure such as factories, warehouses and paved roads has reduced the surface area available for infiltration, and the increased runoff causes erosion on bare soils and siltation of waterways in the lower parts of the wetlands. It was until 2005 that the government of Rwanda started to establish the clear linkages between development and sustainable wetland. In this regard, the Rwanda government promulgated the Organic Law on Environmental Management and established the agency charged with supervision, follow-up and ensuring of environment mainstreaming in all national and local policies. The policymaking has continued to focus on the importance of the Gikondo Wetland. Following the publication Sustainable Development Goals, specifically the SDG 11 on “Make cities inclusive, safe, resilient and sustainable and its inclusion in the National Strategy for Transformation NST1 in its objective 6 on “Sustainably exploit natural resources and protect the environment”, The Gikondo Wetland received the policy attention due to its functions and services. This shows that the motive to restore this wetland is enshrined in the above international, national and local policies. This calls for the need to provide decision making on historical evolution of the functions and services of the Gikondo Wetland to guide future decision making in the restoration and sustainable use of this wetland. However, there have been few studies on the integration of the Gikondo Wetland restoration in the sustainable urban management of Kigali. For instance, Bizimana & Schilling, (2010) have studied the flood risks and stressed the importance of integrating flooding risks in Kigali Master Plan. Kabanda, (2008)has analysed the level of environmental compliance to organic law in Gikondo wetland. His study demonstrated not only the low level of compliance, high level of violation and lack of capacity to monitor the violation in Gikondo Wetland. Etale,(2011)has studied the risks of cadmium and lead uptake from agriculture products farmed in Gikondo Wetland and demonstrated that high Cadmium and Lead concentration exceeding the EUstandard. In the same vein, Sekomo et al., (2011)have analysed pollution level in Nyabugogo Wetland, and showed that pollutant from Gikondo Industrial Park were discharged without treatment in Nyabugogo Wetland. In sum, these studied have demonstrated environmental and health risks posed by inefficient management of the wetland. However, none of them has shown the spatial dynamics of these risks through a spatio-historical perspective. Therefore, this study aims at using geo-spatial technology to unravel historical dynamics of the degradation of Gikondo wetland to guide future decision in the sustainable use of Gikondo Wetland.
Conclusion
Geospatial technologies based on Geographic Information System and Remote Sensing have the potential to contribute to the understanding of historical and spatial changes in wetland ecosystems services. The use of geo-spatial techniques has shown how the land use change resulted in the degradation of wetland as results of lack of policy integration and coordination in urban planning. This resulted in the increase inbuilt up area at the expense of the wetland area from 1987 to 2009. The same techniques also were able to show that it is possible to monitor the shift inland use policy. They demonstrated that the implementation of a comprehensive legal and institutional framework resulted in the increase in wetland area at the expense of other land use. This means that this shift which is interpreted as the integration of wetland in urban planning policies and related policy coordination has benefit to the resilience of wetland ecosystems in the urban context. Geospatial techniques have demonstrated that changes that are contributing to the recovery of wetland services have been taking place since 2010. Despite the strength of geospatial techniques, this study has only focus on their application in tracking historical and spatial changes using the land cover/ land use change perspective. The latter has not allowed to track change in water (flooding and drying), and biological and chemical concentration of pollutants. It is imperative that the interpretation inland use/ land cover change be combined with change in moisture and pollution concentration to fully grasp how the restoration in Gikondo Wetland is contributing to the recovery of ecosystems services. There is a need of interdisciplinary study to analyse these changes. This study will not only analyse past change but also future changes resulting from the restoration and recreation use of the Gikondo Wetland.