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Mangrove Ecosystem
Timber, Fuelwood &
Charcoal
Harvesting wood has been
identified as the main
driver to mangrove
deforestation in Western
Africa (1.4) and parts of
South Asia (1.5)
$ 744,000 per annum in the
Sundarban reserves in India
and Bangladesh
Flood, storm and erosion
control, prevention of
saltwater intrusion, carbon
sequestration
Global mangrove coastal
protection was valued at
US$ 69.9billion (2009)
Carbon sequestration →
carbon credits →
Voluntary Carbon Markets
→ revenue to communities
Breeding spawning and
nursery
Act as critical habitats and
have been observed to
improve nearby coral reef
fish abundance
Estimated that 1 hectare of
mangroves improved
commercial fisheries
output by1.86 tonnes per
year
Annual economic value can
range anywhere between
US $ 42- 37,500
Tourism, education,
worship
Tourist attractions revolve
around mangrove
Education and research are
important cultural services
of these ecosystems
Malaysian and Iranian
mangrove estimated at an
added tourism value of US
$ 1 million and $ 7 million
per year
Adanguidi et al., (2020)
Islam and Bhuiyan (2018)
Uddin et al., (2013)
Barbier (2006); Locatelli et al., (2014)
Mazda et al., 2006; Plan Vivo (n.a)
Sanford (2009); Ullman et al., 2013
Verra (n.a)
Anneboina and Kavi Kumar (2017);
Carrasquilla-Henao et al., (2019);
DebRoy and Jayaraman (2012); Rönnbäck
(1999)
Ahmad (2007); Dehghani et al., (2010)
Friess (2016); Spalding and Parret (2019);
Uddin et al., (2013)
Provisioning
Services
Regulating
Services
Supporting
Services
Cultural
Services

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Ocean-Climate Finance

  • 1. Mangrove Ecosystem Timber, Fuelwood & Charcoal Harvesting wood has been identified as the main driver to mangrove deforestation in Western Africa (1.4) and parts of South Asia (1.5) $ 744,000 per annum in the Sundarban reserves in India and Bangladesh Flood, storm and erosion control, prevention of saltwater intrusion, carbon sequestration Global mangrove coastal protection was valued at US$ 69.9billion (2009) Carbon sequestration → carbon credits → Voluntary Carbon Markets → revenue to communities Breeding spawning and nursery Act as critical habitats and have been observed to improve nearby coral reef fish abundance Estimated that 1 hectare of mangroves improved commercial fisheries output by1.86 tonnes per year Annual economic value can range anywhere between US $ 42- 37,500 Tourism, education, worship Tourist attractions revolve around mangrove Education and research are important cultural services of these ecosystems Malaysian and Iranian mangrove estimated at an added tourism value of US $ 1 million and $ 7 million per year Adanguidi et al., (2020) Islam and Bhuiyan (2018) Uddin et al., (2013) Barbier (2006); Locatelli et al., (2014) Mazda et al., 2006; Plan Vivo (n.a) Sanford (2009); Ullman et al., 2013 Verra (n.a) Anneboina and Kavi Kumar (2017); Carrasquilla-Henao et al., (2019); DebRoy and Jayaraman (2012); Rönnbäck (1999) Ahmad (2007); Dehghani et al., (2010) Friess (2016); Spalding and Parret (2019); Uddin et al., (2013) Provisioning Services Regulating Services Supporting Services Cultural Services

Editor's Notes

  1. Mangroves have a global coverage of approximately 4.06 billion hectares (FAO,2020A). Provisionary: They are recognised to have several provisionary services which include provision of timber, fuelwood and charcoal to local communities. Consequent, overharvesting has been identified as the main driver of deforestation in parts of Western Africa (Adanguidi et al., 2020) and South Asia (Islam and Bhuiyan, 2018), and through its provisionary services adds value to local economies, eg. annual revenue of US $744,000 in the Sundarban reserves in India and Bangladesh (Uddin et al., 2013). Regulatory: Global mangrove coverage provides protection from floods, storms, erosion, saltwater intrusion (Mazda et al., 2006), which have been valued globally at US $ 69.9 billion (Sanford, 2009). Awareness on mangroves role in coastal protection was popularised after the 2004 tsunami as it could have drastically mitigated the negative effects of the tsunami with sufficient mangrove maintenance (Mazda et al., 2006; Sanford, 2009). The estimation of mangrove value over 20 years of coastal protection and stabilisation service was approximated at US $12,263/ha and the cost of damages of a 1 km² loss in mangroves was around $1879/ha  in Thailand (Barbier, 2006). Using the Voluntary Carbon Markets, mangrove ecosystems have been used to generate income for local communities using sale of carbon credits corresponding to carbon sequestration services (Verra, n.a, Plan Vivo, n.a) and have been identified as strong candidates for payment for ecosystem services (PES) (Locatelli et al., 2014). These mechanisms help fund conservation, protect mangroves and sequester carbon. However, there are only a few blue carbon projects generating carbon credits as it requires further climate market mechanisms (Ullman et al., 2013). Supporting: Mangrove ecosystems provide critical supporting functions as feeding grounds and spawning grounds, and as a consequence decrease predation risk for many fish species and have been observed to improve nearby coral reef fish abundance (Carrasquilla-Henao et al., 2019). In India, it was estimated that the marginal effect of 1 hectare of mangroves on fisheries output is 1.86 tonnes per year towards commercial marine fisheries (Anneboina and Kavi Kumar, 2017). Annual economic value addition to the local fisheries for one hectare of mangrove can range anywhere between US $42-US $37,500 depending on the location, species value, proximity to fisheries from the mangrove etc (DebRoy and Jayaraman, 2012).  Additionally, annual economic value addition per hectare for penaeid shrimp (most economically viable fisheries associated with mangrove) ranges from US $91- US $5292. Cultural: Finally, mangroves through tourism (Spalding and Parret, 2019), education (Friess, 2016) and cultural practices (worship) adds further value. It was estimated to add US $1 million and US $7 million annually to the Malaysia and Iranian tourism revenue (Ahmad, 2007; Dehghani et al.,2010) and US $42,000 annually in the Sundarban reserves in India and Bangladesh (Uddin et al., 2013).