Conference PaperPDF Available

Deforestation and degradation of mangroves in the Niger Delta Region of Nigeria: Implications in a changing climate

Authors:

Abstract and Figures

The mangrove forest ecosystem in addition to acting as a buffer to extreme weather events, contributes immensely to the socio-economic well-being of the coastal communities. However, this important ecosystem is fast diminishing in the Niger Delta Region of Nigeria due to factors which are mainly anthropogenic. This study investigated the factors responsible for mangrove deforestation and degradation in this region, and x-rayed the consequences in a rapidly changing climate. It was observed that land reclamation for building of settlements, fish farming, road construction, electricity projects, timber/fuel-wood gathering, oil exploration/exploitation and related activities, refuse dumping, and Nypa fruticans invasion, are among the causes of mangrove deforestation and degradation in the region. The paper posits that climate change impact will be more severe in the region, as the ecological, socio-economic, and adaptive roles of the mangroves are lost through deforestation and degradation. Strict protection of the remaining mangrove forests and the regeneration of deforested and degraded mangroves are recommended, for the sustenance and enhancement of their roles in climate change mitigation and adaptation, and the socio-economic well-being of the coastal communities.
Content may be subject to copyright.
Chima, U. D. and Larinde, S. L. 521
DEFORESTATION AND DEGRADATION OF MANGROVES IN THE
NIGER DELTA REGION OF NIGERIA: IMPLICATIONS IN A
CHANGING CLIMATE
Chima, U. D.* and Larinde, S. L.
Department of Forestry and Wildlife Management, University of Port
Harcourt, P.M.B. 5323, Port Harcourt, Rivers State, Nigeria
Abstract
The mangrove forest ecosystem in addition to acting as a buffer to extreme weather events,
contributes immensely to the socio-economic wellbeing of the coastal communities. However, this
important ecosystem is fast diminishing in the Niger Delta Region of Nigeria due to factors which
are mainly anthropogenic. This study investigated the factors responsible for mangrove
deforestation and degradation in this region, and x-rayed the consequences in a rapidly changing
climate. It was observed that land reclamation for building of settlements, fish farming, road
construction, electricity projects, timber/fuel-wood gathering, oil exploration/exploitation and
related activities, refuse dumping, and Nypa fruticans invasion, are among the causes of mangrove
deforestation and degradation in the region. The paper posits that climate change impact will be
more severe in the region, as the ecological, socio-economic, and adaptive roles of the mangroves
are lost through deforestation and degradation. Strict protection of the remaining mangrove forests
and the regeneration of deforested and degraded mangroves are recommended, for the sustenance
and enhancement of their roles in climate change mitigation and adaptation, and the socio-
economic wellbeing of the coastal communities.
Keywords: Niger Delta, mangrove, deforestation, climate change, impact, adaptation.
*Corresponding author (uzoma.chima@uniport.edu.ng)
Introduction
The mangrove forest is typically a tropical group of salt tolerant plants that occupy the
inter-tidal zone of sheltered coasts around estuaries and lagoons. The mangrove forests
are known to serve various socio-economic and ecological functions especially in the
coastal communities. For instance, they provide breeding grounds for fish species and
provide numerous non-wood products that contribute to rural livelihoods.
However, the African mangroves have suffered much pressure in the recent past with
enormous losses. The loss, destruction and degradation of the mangrove forests have
been attributed to many factors including urbanization, quarrying, salt and sand
extraction; pollution from industries, agro-industrial chemicals, petroleum and gas
exploitation; absence of appropriate legislation; deforestation for fish smoking (Ajonina
and Usongo, 2001; Ajonina et al, 2005).
522 38th Annual Conference of Forestry Association of Nigeria (FAN)
The Nigerian mangrove forest belt, besides contributing to the socio-economic wellbeing
of the rural coastal communities, has the potential to protect them against extreme
weather events orchestrated by climate change. Rising sea level is envisaged to increase
flooding in low lying coastal areas, which will in turn increase the physical and socio-
economic vulnerability of coastal cities. Nigeria has been recognised as one of the most
vulnerable African countries to climate change and the impacts are already being felt in
different parts of the country.
Nigeria has over 2,000 industrial establishments with about 80% of these concentrated in
the coastal zone especially urban centres, mainly in Lagos, Port Harcourt, and their
environs. Industries located in the Nigerian coastal zone include: oil and gas,
petrochemical, iron and steel, fertilizer plant, aluminum smelting plant and
manufacturing industries such as textiles, food, plastics, pharmaceuticals, cement, soaps
and detergents, paints, brewing, and wood pulp and paper(FEPA, 1997).
With the majority of Nigeria’s total industrial establishments in the coastal States and
more people living and working in climate change-prone areas in the country, the
consequences of mangrove deforestation and degradation cannot be underestimated. This
paper therefore investigated the causes of mangrove deforestation and degradation in the
Niger Delta Region of Nigeria, and examined the implications in a rapidly changing
climate.
Methodology
Field trips spanning coastal communities in purposively selected States Rivers,
Bayelsa, and Ondo, within the Niger Delta Region of Nigeria, were embarked upon in
2010 and 2015, to ascertain the causes and consequences of mangrove deforestation and
degradation in the study area. In addition, information available from relevant scientific
literature on the subject matter was used.
Distribution and Extent of the Mangrove Forest in Nigeria
The distribution of mangroves is affected by climatic factors like temperature and
moisture (Duke 1992; Saenger and Snedaker 1993), and other coastal processes like tidal
mixing and coastal currents, which affect the dispersal of propagules (De Lange and De
Lange 1994). Agrawala et al. (2003), noted that the richest mangrove communities occur
in areas with water temperature in the warmest month greater than 24oC; while Aizpuru
et al. (2000) observed that most are found within latitude 25° north and south of the
equator, covering approximately 17 million ha in 112 countries and territories in Asia,
Africa, Australia, and the Americas.
Approximately 75 per cent of mangroves are concentrated in just 15 countries; with close
to half of mangrove coverage occurring in five countries Indonesia, Australia, Brazil,
Chima, U. D. and Larinde, S. L. 523
Nigeria and Mexico. Nigeria’s mangrove forest which covers an area of about 105,000
hectares is known to be the largest in Africa and the third largest in the world (World
Bank, 1995 and Ndukwu and Edwin-Wosu, 2007).The Nigerian coastline which is
approximately 853km long stretches from the western border with the Republic of Benin
to the eastern border with Cameroon, with mangroves and estuaries extending from 10-
150 km inland (USAID, 2008). Mangroves are found in all the coastal states of Nigeria
namely – Akwa-Ibom, Bayelsa, Cross River, Delta, Edo, Lagos, Ogun, Ondo, and
Rivers States (Figure 1). However, the extent of mangroves in these states varies with
Rivers/Bayelsa having the largest area of mangroves (Table 1).
Niger
Borno
Sokoto
Yobe
Bauchi
Taraba
Plateau
Oyo
Kebbi
Kogi
Kaduna
Kwara
Edo
Benue
Kano
Ondo
Adamawa
Jigawa
Katsina
Delta
Rivers
Ogun
Enugu
Cross River
Osun
Abia
Imo
Lagos
Akwa Ibom
Anambra
FCT
Nigerian States
Mangrove Forest
200 0 200 400 Kilometers
N
MANGROVE FOREST OF NIGERIA
Figure 1: Map of Nigeria showing the distribution of the mangrove forest
524 38th Annual Conference of Forestry Association of Nigeria (FAN)
Table1: Distribution of Mangrove Forest in the Nigerian Coastal Area
State
Area of Mangrove (Km
2
)
Mangrove in Forest Reserves
Area (Km
2
)
% of total
Lagos
42.20
3.13
7.42
Ogun
12.18
-
-
Ondo
40.6
2
-
-
Edo/Delta
3,470.32
143.75
4.14
Rivers /Bayelsa
5,435.96
90.62
1.67
Cross
River/Akwa Ibom
721.86
67.19
9.31
TOTAL
9,723.14
304.69
-
Source: Adapted from (NEST, 1991)
The Nigerian mangrove is dominated by the red mangroves (Rhizophoraceae), in
association with white mangroves (Avicenneaceae). The red mangrove Rhizophora
racemosa, is the most common species, covering over 90% of the area and can grow to a
height of 45 m under favourable conditions. It is the pioneer species, and is followed by
R. harrisonii and R. mangle as the land gets drier and salinity decreases. Avicennia
species, a smaller tree than Rhizophora species, grows singly on firm land.
As confirmed by Figure 1 and Table 1, much of the Nigeria’s mangrove forest is found in
the Niger Delta region, and the mangrove in this area, has been reported to be the most
exploited in the world (FAO, 2007). The pressure on the mangrove ecosystem, which was
minimal, during the pre-colonial era due to low population densities and subsistence
agriculture (Bisong, 2001), has been exacerbated by the burgeoning human population
and the concomitant activities, including oil exploration and exploitation (Mmom, 2007).
The major factors responsible for the destruction of the Nigerian mangroves are discussed
in detail in the subsequent section.
Causes of Mangrove Deforestation and Degradation in the Niger Delta Region
Several factors are responsible for the deforestation and degradation of the mangrove
forest in the Niger Delta Region of Nigeria. These include land reclamation for building
of settlements, fish farming, road construction, electricity, logging for timber, fuelwood
gathering, oil exploration/exploitation and related activities, refuse dumping, and Nypa
fruticans invasion.
Development of Infrastructure
This is a major cause of mangrove deforestation in the Niger Delta Region of Nigeria. In
recent times especially with the creation of the Niger Delta Development Commission
(NDDC) following so many years of struggle and campaign against marginalization of
Chima, U. D. and Larinde, S. L. 525
the people of the Niger Delta Region (where Nigeria’s crude oil is mainly found), some
efforts have been made to develop infrastructure, and these sometimes result to the
destruction of the mangroves. Plates 1 and 2 respectively show the destruction of
mangrove forest and subsequent sand-filling as the Ogbia-Nembe road was being
constructed in Bayelsa State. These activities sometimes introduce and encourage the
growth of some species alien to the mangrove environment around it (see Plate 3).
Plate 1: Destruction of the mangrove for the construction of Ogbia-Nembe road,
Bayelsa State
Source: Field survey, 2010.
Plate 2: Sand-filling of destroyed mangrove area, Ogbia-Nembe road construction,
Bayelsa State
Source: Field survey, 2010.
526 38th Annual Conference of Forestry Association of Nigeria (FAN)
Plate 3: Musanga cecropioides growing on topsoil deposited in a mangrove swamp
forest by the grader near Agip Canal during the construction of Ogbia-Nembe road,
Bayelsa State.
Source: Field survey, 2010.
Land reclamation for building of settlements and public facilities is also another major
threat to the mangrove ecosystem in the Niger Delta region of Nigeria. In many parts of
the region, the mangrove forest is being cleared to build residences (Plate 4) and other
public facilities like schools (Plate 5), especially in mangrove areas that are close to
access roads.
Plate 4: Mangrove deforestation to reclaim land for residential buildings, Buguma,
Rivers State
Source: Field survey, 2015.
Chima, U. D. and Larinde, S. L. 527
Plate 5: Land reclamation from mangroves for the construction of a model
secondary school in Buguma, Rivers State.
Source: Field survey, 2015.
Electricity Projects sometimes result to the destruction of the mangrove forest (Plate 6).
Laying of high-tension wires for electricity projects in mangrove areas leads to mangrove
deforestation and degradation in some cases.
Plate 6: Mangrove destruction for electricity projects, Buguma, Rivers State
Source: Field survey, 2015.
528 38th Annual Conference of Forestry Association of Nigeria (FAN)
Fish Farming
Large scale fish farming is one of the factors responsible for mangrove deforestation and
degradation in the Niger Delta region of Nigeria. A very good example is seen in
Buguma, Rivers State (Plate 7) where ONIDA – an Israeli company is involved in large-
scale fish farming. The construction of the fish farm (with over forty ponds) led to the
destruction and sand-filling of a large expanse of the mangrove forest on which rural
livelihood depends to some reasonable extent. The major interest in sitting the farm near
the mangrove is constant provision of brackish water required to grow the fish species of
interest – Barramundi (Plate 8), which is bred and imported from Australia. One wonders
what the contributions of such a venture are, especially to the rural economy, as virtually
everything used in the farm including fish feed, is being imported from either Israel or
Australia.
Plate 7: Mangrove deforestation for large scale fish farming in Buguma, Rivers
State
Source: Field survey, 2015.
Plate 8: Barramundi – an exotic fish species reared by an Israeli company –
ONIDA, in Buguma, Rivers State
Source: Field Survey, 2015
Chima, U. D. and Larinde, S. L. 529
Timber and Fuel Wood Gathering
The mangrove forest is a source of timber. The mangrove species are widely used as fuel
for firing small scale industrial boilers due to its high thermal capacity. The red mangrove
Rhizophora racemosa, is the most exploited species and is used for firewood, poles and
timber. The destruction of the mangrove for fuelwood gathering (Plate 9) is on the
increase in many parts of the Niger Delta to meet household energy needs and for income
generation.
Plate 9: Destruction/degradation of mangroves via fuel-wood gathering
Source: Field survey, 2015.
Oil Exploration/Exploitation and related Activities
Activities of the oil and gas industry in the mangrove forests of the Niger Delta (Figure 2)
are to a large extent responsible for mangrove fragmentation, deforestation and
degradation. Oil drilling and spillage, dredging of canals, and construction of residential
quarters for oil workers, constitute huge threat to the survival and proper functioning of
the mangrove ecosystem in the Niger Delta region. O’Neil (2007) observed that oil spills
and leakages have destroyed much of the Nigeria’s mangrove areas including the fishing
economy and water quality.
530 38th Annual Conference of Forestry Association of Nigeria (FAN)
Figure 2: Crude oil pipeline network in the Niger Delta Region
Source: Niger Delta Regional Plan 2005.
The Menace of Nipa palm
Nypa fruticans (Nipa palm) – an invasive alien species (Plate 10), is another major threat
to the mangrove ecosystem in the Niger Delta Region. The species which was introduced
in Nigeria for the control of river bank erosion has become a big menace to the mangrove
ecosystem. The deforestation and degradation of the mangroves for firewood gathering,
the construction of navigational canals, villages, and the activities of oil companies,
encourage their replacement by this fast colonizer (Nypa fruticans) which does not
provide the enormous ecological services provided by mangroves (USAID, 2008).
Tackling the menace of Nipa palm invasion of the mangrove ecosystem requires a
holistic approach that will discourage mangrove deforestation and degradation, complete
removal of the species in invaded areas, and massive regeneration of degraded
mangroves. SCBD (2001) observed that restoration of degraded habitats in addition to re-
introduction of native species can enhance biological diversity and also enhance the
resilience of ecosystems against future invasions. Efforts should also be made towards
discovering other uses of the Nipa palm that will be beneficial to man.
Chima, U. D. and Larinde, S. L. 531
Plate 10: Nypa fruticans (Nipa palm) – a fast colonizer that threatens the mangrove
ecosystem
Source: Field survey, 2015.
Other Factors
Defecation, refuse dumping, and unsustainable exploitation of non-wood resources, are
also among the factors responsible for mangrove degradation in the Niger Delta region.
The construction of public toilets that empty directly into the mangroves and the dumping
of refuse in and near the mangroves (Plate 11) are now common in the region.
Unsustainable exploitation of non-wood resources like fish, periwinkle, crab, etc. is also
worrisome.
532 38th Annual Conference of Forestry Association of Nigeria (FAN)
Plate 11: Public toilets and refuse dumping in mangroves
Source: Field survey, 2015.
Another factor that encourages the loss and degradation of the mangrove forests in the
Niger Delta is the palpable weakness in the implementation of the Environmental Impact
Assessment (EIA) decree. Sometimes projects are executed before EIA is done, and in
some cases where they are done prior to the execution of the project, the process is
usually replete with irregularities that are allowed by the representatives of relevant
agencies that should ensure due process and maintain standards. In some cases, clearance
is given for projects with huge potential negative impacts on the environment. Here in the
Niger Delta Region, multinational oil companies get away with pollution and spillage in
many places including the marine and coastal ecosystems unlike in most developed
countries. There is need for strict adherence to and compliance with the provisions of the
EIA decree if sustainable development is to be guaranteed.
Implications of Mangrove Deforestation and Degradation in a Changing Climate
The implications of mangrove deforestation and degradation in the Niger Delta Region of
Nigeria are quite grave especially in the light of the vulnerability of the region to climate
change. In this paper, these implications are considered in respect of climate change
mitigation and adaptation, and the socio-economic consequences of extreme weather
events orchestrated by climate change.
Implications for Climate Change Mitigation
The role of mangrove forests in climate change mitigation has been acknowledged the
world over. The mangrove forests are among the most carbon-rich tropical forests
Chima, U. D. and Larinde, S. L. 533
(Donato et al., 2011), due to high levels of plant production in addition to high levels of
sedimentation from rivers and tidal inputs (Kristensen et al., 2008). Annual mean carbon
sequestration rate of the mangrove has been known to exceed those of the terrestrial
forest ecosystems like the tropical rain forest, the temperate rain forest and the boreal
forests (McLeod et al., 2011). Unlike in most terrestrial ecosystems, the mangrove
ecosystems store about 50 90 % of their carbon below ground where it can remain for
very long periods, with the remainder equally stored for long periods of time in the wood
(Pan et al. 2011; Pendleton et al., 2012). As a result, more carbon is released to the
atmosphere and the ocean when mangroves are degraded or converted to other land uses
compared with the terrestrial ecosystems. Donato et al. (2011) estimated that mangrove
deforestation generates emissions of 0.02-0.12 Pg carbon per year as much as around
10% of emissions from deforestation globally, despite accounting for just 0.7% of
tropical forest area. Thus, as the mangrove forests are destroyed in the Niger Delta
Region, they not only release the carbon they hold but also lose their potential to
sequester more carbon in the future.
Implications for Climate Change Adaptation
It has been documented that climate change will have considerable impacts in coastal
regions (Bardsley, 2006; Caton, 2007), which will probably include beach and dune
erosion due to the effects of rising sea levels, extreme events, changes to run-off patterns,
and flooding (Caton, 2007). Many coastal communities in different parts of the world
have already started experiencing some of these impacts with their concomitant colossal
damages and losses.
However, the mangrove forests and other marine and coastal ecosystems like sea-grass
meadows, mangroves, and tidal marshes, provide services that aid adaptation to climate
change impacts along the coast. These services include prevention of shoreline erosion,
protection from storms and sea level rise, regulation of coastal water quality, and food
security for many coastal communities around the world. They also protect adjacent
marine ecosystems (often coral reefs) from terrestrial inputs, and provide habitat for
diverse fish and invertebrates, some of which are commercially important (Rützler and
Feller 1996; Mumby et al. 2004).
Therefore the current rate of mangrove deforestation and degradation in the Niger Delta
Region without any attempt at regeneration will definitely increase the vulnerability of
coastal communities in the area, to extreme weather events. There are clear evidences in
several parts of the world to buttress this assertion. Evidences from the countries affected
by the 2004 Tsunami confirmed that mangrove forests played crucial roles in saving lives
and property, and that the waves penetrated far inland where mangroves and other coastal
ecosystems had been destroyed, resulting to flooding of farms, destruction of homes and
means of livelihood (EJF, 2006). The four countries Indonesia, Sri Lanka, India and
534 38th Annual Conference of Forestry Association of Nigeria (FAN)
Thailand, that were worst hit by the impacts of the 2004 Tsunami lost 28% of their
mangrove forests between 1980 and 2000 (EJF, 2006). It is also widely acknowledged
that the destruction of mangroves and reefs exacerbated the damages done by the 2005
Hurricane Katrina to the US coastal States.
Socio-Economic Implications
The socio-economic consequences of mangrove deforestation and degradation are quite
enormous. Although there are no particular estimates or figures for Nigeria, UNEP
(2014) reported that the variety of goods and services provided by mangrove forests
worth an estimated US$33-57,000 per hectare per year to the national economies of
developing countries with mangroves; and that over 100 million people that live within
10 kilometres of large mangrove forest benefit from them. In addition, emissions
resulting from mangrove losses make up nearly one fifth of global emissions from
deforestation, resulting in economic damages of US$6–42 billion annually (UNEP,
2014). Other socio-economic implications may include effects on public health,
employment and income generation, changes in population and ethnic patterns, and needs
for resettlement of families affected by extreme weather events.
Although there are no studies that have quantified the monetary contributions of the
mangroves (in terms of the goods and services provided) to the Nigerian economy,
mangroves provide tangible goods like fuel-wood, crabs, shrimps, honey, medicine, dyes,
thatch, salt and periwinkles, which support rural livelihoods and serve as vital sources of
income to the rural dwellers especially in coastal communities. In addition to the above
tangible goods, the mangroves provide intangible services by buffering the coastal
communities and providing breeding grounds for fishes.
The economic implications of mangrove deforestation and degradation in the Niger Delta
Region cannot be overemphasized, given the fact that the oil companies which contribute
immensely to the wealth of the Nigerian nation is located mostly in this region. Lubeck et
al. (2007) reported that there are over 600 oil fields, 5,284 on- and- off shore oil wells, 10
export terminals, 275 flow stations, 4 refineries and an LNG project, in the Niger Delta
Region. In addition to these are other subsidiary companies and investments, and the
teaming human population in the region. Therefore, with current high spate of mangrove
destruction, extreme weather events orchestrated by climate change, are bound to cause
colossal and monumental economic damages.
What Should be Done?
The importance of mangrove ecosystems in climate change mitigation and adaptation
(especially in coastal areas) cannot be overemphasized. Hence, the need for the Nigerian
Government to come up with appropriate laws and policies that will halt the current high
spate of mangrove degradation and conversion, conserve the remaining mangroves, and
Chima, U. D. and Larinde, S. L. 535
ensure massive regeneration of degraded areas. These will help to improve the resistance
of mangrove ecosystems to climate change so that they can continue to deliver ecosystem
services, and provide alternative livelihood options in the face of climate change. Mant et
al. (2014) observed that the conservation, restoration and sustainable management of
ecosystems can help reduce vulnerability to climatic hazards such as hurricanes, rising
sea levels, floods and droughts.
It is imperative to ensure that EIAs are thoroughly done for developmental projects in the
Niger Delta region to mitigate the high spate of destruction and degradation of very
important ecosystems like the mangrove forest. In addition, environmental impacts of
industries sited in coastal regions can be mitigated by ensuring that their wastes are
treated to specified and acceptable standard before they are discharged into the sea.
In addition, Nigeria should emulate other countries like Indonesia, Philippines,
Bangladesh, and Sri Lanka, where mangrove regeneration has become a very serious
business. Apart from direct planting of mangrove species, efforts to conserve the
mangroves in these countries include environmental education of the coastal communities
on the need for sustainable use.
Conclusion and Recommendation
Mangrove forests in the Niger Delta region of Nigeria have been deforested and degraded
to a large extent due mainly to anthropogenic pressures. There is need for mapping and
strict protection of the remaining mangrove forests in the region. Massive regeneration of
deforested and degraded mangrove areas should be carried out urgently, for enhanced
ecological roles, socio-economic wellbeing of the people, and climate change
adaptation/mitigation. There appears to be paucity of information from the available
literature concerning the ecology of mangrove ecosystems in Nigeria, their carbon
sequestration capabilities/potential, economic values, and current status. There is a dire
need for empirical studies to fill these gaps.
References
Agrawala, S., Ota, T, Risbey, J., Hagenstad, M, Smith, J., Van Aalst, M., Koshy, K. and
Prasad, B. 2003. Development and climate change in Fiji: Focus on coastal
mangroves. Environment Directorate and Development Cooperation Directorate,
Organisation for Economic Cooperation and Development (OECD, Paris. Report no.
COM/ENV/EPOC/DCD/DAC (2003)4/FINAL.
Ajonina, G.N. and Usongo, L. 2001. Preliminary quantitative impact assessment of wood
extraction on the mangroves of Douala-Edea Forest Reserve Cameroun. Tropical
Biodiversity 7(2 & 3): 137-149.
Ajonina, P.U., Ajonina, G.N., Jin, E. Mekongo, F., Ayissi, I. and Usongo, L. 2005.
Gender roles and economics of exploitation, processing and marketing of bivalves
536 38th Annual Conference of Forestry Association of Nigeria (FAN)
and impacts on forest resources in the Douala-Edaa Wildlife Reserve, Cameroon.
International Journal of Sustainable Development and World Ecology 12: 161- 172
Aizpuru, M., Achard, F., and Blasco, F., 2000. Global assessment of cover change of the
mangrove forests using satellite imagery at medium to high resolution. In: EEC
Research project, FIED ISP FR – Joint Research Centre, Ispra.
Bardsley, D. 2006. There's a change on the way An initial integrated assessment of
projected climate change impacts and adaptation options for Natural Resource
Management in the Adelaide and Mt Lofty Ranges Region, DWLBC Report 2006,
Government of South Australia, Department of Water, Land and Biodiversity
Conservation, Adelaide.
Bisong F. E. 2001. Natural resource use and conservation system for sustainable rural
development. BAAJ International Coy, Calabar.
Caton, B. 2007. The Impact of Climate Change on the Coastal Lands of the City of
Onkaparinga, City of Onkaparinga, South Australia, 61pp.
De Lange, W.P. and P.J. De Lange 1994. An appraisal of factors controlling the
latitudinal distribution of mangrove (Avicennia marina var. resinifera) in New
Zealand. Journal of Coastal Research 10 (3): 539-548.
Donato, D.C., Kauffman, J.B., Murdiyarso, D., Kurnianto, S., Stidham, M. and Kanninen,
M. 2011. Mangroves among the most carbon-rich forests in the tropics, Nature
Geoscience, 4:293-297.
Duke, N.C. 1992. Mangrove floristics and biogeography. In: Robertson A.I. and Alongi,
D.M. (Eds.) Tropical Mangrove Ecosystems. American Geophysical Union,
Washington DC., USA, pp. 63-100.
EJF (Environmental Justice Foundation) 2006. Mangroves: Nature’s defence against
Tsunamis – A report on the impact of mangrove loss and shrimp farm development
on coastal defences. Environmental Justice Foundation, London, UK. 33pp.
FAO (Food and Agriculture Organization of the United Nations) 2007. The world’s
mangroves 1980-2005. FAO Forestry Paper 153. FAO, Rome.
FEPA 1997. Coastal Profile of Nigeria. Federal Environmental Protection Agency Large
Marine Ecosystem Project for the Gulf of Guinea. 87pp.
Kristensen, E., Bouillon, S., Dittmar, T., Marchand, C. 2008. Organic carbon dynamics in
mangrove ecosystems: A review, Aquatic Botany, 89: 201-219.
Lubeck, P., Watts, M. and Lipschutz, R. 2007. Convergent Interest: US Energy Security
and the Securing of Nigeria’s Democracy. International Policy Report, Centre for
International Policy, Washington DC.
Mant, R., Perry, E., Heath, M., Munroe, R., Väänänen, E., Großheim, C., and Kümper-
Schlake, L. 2014. Addressing climate change – why biodiversity matters. UNEP-
WCMC, Cambridge, UK
McLeod, E., Chmura, G.L., Bouillon, S., Salm, R., Bjork, M., Duarte, C.M., Lovelock,
C.E., Schlesinger, W.H. and Silliman, B.R. 2011. A blueprint for blue carbon: toward
an improved understanding of the role of vegetated coastal habitats in sequestering
CO2. Frontiers in Ecology and the Environment 9: 552-560.
Chima, U. D. and Larinde, S. L. 537
Mmom, P.C. 2007. Impact of Human Density and Economic Activities on the Mangrove
forest of the Niger Delta, Nigeria. Paper presented at the Annual Conference of the
International Association for Impact Assessment, held in Seoul South Korea. 1-9th
June, 2007.
Mumby, P. J., Edwards, A.J. and Aris-Gonzalez, J.E., Lindeman, K.C., Blackwell, P.G.,
Gall, A., Gorczynska, M.I., Harborne, A.R., Pescod, C.L., Renken, H., Wabnitz,
C.C.C. and Llewellyn, G. 2004. Mangroves enhance the biomass of coral reef fish
communities in the Caribbean. Nature 427:533-536.
Ndukwu, B.C. and Edwin-Wosu, N.L. 2007. Changes in species diversity due to dredged
spoils in the mangrove forest of the Niger Delta, Nigeria.
NEST 1991. Nigeria’s Threatened Environment: A national profile. Nigeria
Environmental Study/Action Team, Ibadan, Nigeria.
Niger Delta Development Commission (NDDC). 2005. Draft copy of the Niger Delta
Regional Development Master Plan. Directorate of Planning: NDDC, Port Harcourt.
O’Neill, T. 2007. Curse of the Black Gold: Hope and betrayal in the Niger
Delta. National Geographic 211 (2): 88-117.
Pan, Y., Birdsey, R.A., Fang, J., Houghton,R., Kauppi, P.E., Kurz, W.A., Phillips, O.L.,
Shvidenko, A., Lewis, S.L.., Canadell, J.G., Ciais, P., Jackson, R.B., Pacala, S.,
McGuire, A.D., Piao, S., Rautiainen, A., Sitch, S. and Hayes, D. 2011. A large and
persistent carbon sink in the world’s forests. Science 333: 988-993.
Pendleton, L., Donato, D.C., Murray, B.C., Crooks, S., Jenkins, W.A., Sifleet, S., Craft,
C., Fourqueran, J.W., Kauffman, J.B., Marbà, N., Megonigal, P., Pidgeon, E., Herr,
D., Gordon, D. and Balder, A. 2012. Estimating global “Blue Carbon” emissions
from conversion and degradation of vegetated coastal ecosystems. PLoS ONE 7(9):
435-42.
Rützler, K., and Feller C. 1996. Caribbean mangrove swamps. Sci. Amer. 274:94-99.
Saenger, P. and Snedaker. S.C. 1993. Pantropical trends in mangrove above-ground
biomass and annual litter fall. Oecologia 96, 293-299.
Secretariat of the Convention on Biological Diversity 2001. Review of the efficiency and
efficacy of existing legal instruments applicable to invasive alien species. Montreal,
SCBD, 42pp. (CBD Technical Series No. 2).
UNEP 2014. The Importance of Mangroves to People: A Call to Action. van Bochove, J.,
Sullivan, E., Nakamura, T. (eds). United Nations Environment Programme World
Conservation Monitoring Centre, Cambridge. 128pp.
USAID 2008. Nigeria Biodiversity and Tropical Forestry Assessment. United States
Agency for International Development, 90pp.
World Bank. 1995. Defining an Environmental Development Strategy for the Niger
Delta, Vol. II, Industry and Energy Operations Division (West Central Africa
Department), Washington DC.
... En effet, les principales menaces de la mangrove dans l'Océan Indien sont le développement urbain et des colonies (Mitra, 2013). Au Nigéria, le développement des infrastructures, dont la construction de routes, est l'une des causes majeures de déforestation dans le delta du Niger (Chima et Larinde, 2016). La remise en état des terres pour la construction de colonies et d'installations publiques est également une autre menace pour l'écosystème de mangrove dans cette région (Chima et Larinde, 2016). ...
... Au Nigéria, le développement des infrastructures, dont la construction de routes, est l'une des causes majeures de déforestation dans le delta du Niger (Chima et Larinde, 2016). La remise en état des terres pour la construction de colonies et d'installations publiques est également une autre menace pour l'écosystème de mangrove dans cette région (Chima et Larinde, 2016). La dérivation des cours d'eau et la construction de barrage ne sont pas très courantes ; mais, leurs effets sont presque toujours sévères, tels qu'au Bangladesh, en Colombie, au Sénégal ou au Vietnam (Mitra, 2013). ...
... 'Un très bon exemple est vu à Buguma, dans l'État de Rivers, situé dans la région du delta du Niger au Nigéria, où une société est impliquée à grande échelle dans l'aquaculture. Celle-ci a conduit à la destruction et au remplissage de sable d'une grande étendue de la forêt de mangrove (Chima et Larinde, 2016). L'aquaculture n'est pas une pratique très répandue, même si elle est présente dans les trois sites, elle n'occupe généralement que de petites surfaces, les plus importantes étant situées à Angondjé et en amont de l'Igoumié. ...
Article
Full-text available
Malgré leur importance dans la stabilité et la santé des environnements côtiers, les mangroves sont soumises à des pressions importantes, majoritairement causées par des moteurs anthropiques. Les objectifs sont de mesurer la régression des surfaces de mangrove entre 2007 et 2020 dans l’espace urbain du Grand Libreville (Gabon) et d’identifier les moteurs anthropiques de déforestation. Pour cela, deux méthodes complémentaires ont été appliquées : une analyse de la dynamique de l’occupation du sol de trois sites caractéristiques, à partir d’orthophotos à très haute résolution, fournies par Maxar Technologies, et des observations directes. Ainsi, entre 2007 et 2020, les changements d’occupation du sol à Okala-Angondjé, Lowé et Igoumié sont surtout marqués par la progression du bâti et son empiètement sur la végétation. Tous les sites ont connu des régressions nettes de mangrove : 35,6 hectares à Okala-Angondjé, 46,9 hectares à Lowé et 36,6 hectares à Igoumié, donnant lieu à un taux de déforestation global de 0,8% par an. Les reculs d’origine anthropique y représentent 57% des régressions à Okala-Angondjé, 96% à la rivière Lowé et 78% dans la zone d’Igoumié. Les moteurs de déforestation sont multiples : expansions résidentielles, installation de quartiers de pêcheurs, implantations hôtelières ou touristiques, création et extension des décharges d’ordures, industrialisation, développement portuaire et installations énergétiques. D’autres activités économiques ont provoqué aquaculture. Toutefois, le taux annuel de déforestation des mangroves urbaines dans la province gabonaise de l’Estuaire est plus élevé que la moyenne mondiale de déforestation des mangroves (0,11%).
... The mangroves of Nigeria are considered to be critically endangered by the World Wide Fund for Nature (World Bank, 1995). Along with the impact to biodiversity and carbon storage as a result of mangrove loss, it is estimated that climate change impacts will be more severe in this region as ecological, socio-economic and adaptive ecosystem services of mangroves are lost (Chima & Larinde, 2016). ...
Article
Full-text available
Invasive species are a leading threat to biodiversity worldwide. Nypa palm ( Nypa fruticans ) has emerged as the predominant invasive species in the Niger Delta region of Nigeria. While endemic mangroves have high rates of carbon sequestration, stabilize coastlines and protect biodiversity, Nypa does not provide these services outside its native region of Southeast Asia. Oil exploration and urbanization in this region also exacerbate mangrove loss and Nypa spread. As Nypa is difficult to distinguish from endemic mangrove species in remotely sensed data, estimates of mangrove and ecosystem services losses in Nigeria are highly uncertain. Here, we analyse multisensor satellite data with machine learning to quantify the rapid expansion of Nypa from 2015 to 2020 in Nigeria. Using Landsat imagery and random forest classification, we quantify total potential Nypa extent in Nigeria in 2019. We then produced a Nypa extent map using iterative combinations of Sentinel‐1 SAR, Sentinel‐2 MSI and ALOS PALSAR. Random forest classifications using SAR data from ALOS and Sentinel‐1 were best suited for mapping Nypa extent with similar accuracies (78% and 75%, respectively). Based on data availability and accuracy, we focussed our change analysis on Sentinel‐1 SAR. Our results show ~28 000 ha of mangroves were converted to Nypa in Nigeria by 2020 and covered a larger extent than endemic mangroves, compounding the effect of the existing degradation and deforestation in the region. We also compared forest height and complexity estimates from Global Ecosystem Dynamics Investigation LiDAR to further distinguish between endemic mangroves and Nypa in three dimensions. Nypa structural variability, measured by top‐of‐canopy height, vegetation cover, plant area index, and foliage height diversity, was lower than that of mangroves. At current rates of Nypa expansion, the entire area of study would be invaded by Nypa by 2028, with potentially detrimental consequences to the ecosystem services provided by mangroves.
... Food and Agricultural Organization (FAO) (2018) revealed that deforestation contributes to climate change through forest-dependent peoples and society, who in recent times has increased the degree of forest product delivery and forest system services. Chima and Larinde (2016) disclosed that the mangrove forest ecosystem helps to retard extreme weather condition in the coastal communities, however, have gradually diminished in the Niger Delta region due to factors attributed to crude oil exploration and exploitation by the oil companies. The function of mangrove plantations in climate change mitigation has been recognized globally. ...
Article
Full-text available
The study examined the negative effects of climate change on food supply in the Niger Delta region, Nigeria. The variation in weather conditions in the Niger Delta region is principally attributed to anthropogenic activities of the transnational oil companies and artisanal refining in the Region. Presently, the Niger Delta region has experienced a decline in food supply occasioned by high temperature, heavy rainfall, sea-level rise, and flooding emanating from climate change. The study relied on triangulation methods of data gathering techniques. The study administered 400 questionnaires and 20 interviews among respondents in randomly selected clusters in four Niger Delta states while the secondary data was sourced through the internet, journals, and books. Findings revealed that farming and fishing accounted for over 90 percent of the traditional economy of the region. The Region has suffered from environmental degradation emanating from oil production. Consequently, the majority of the crops, forest resources, and seafood in the region have gone into extinction as a result of global warming. The effects of climate change constitute a threat to the existence of many households, who depend on forest resources for their survival. The study concluded that deprivation of the inhabitants from participating in Petrodollar business is one of the reasons for launching artisanal refinery, hence, increased the circulation of greenhouse gas emission in the atmosphere leading to alteration of weather condition and food production.
... Erosion of channel and creek banks are caused mostly by exposing the banks to tidal currents and waves from passing engine boats and vessels. Apart from use for construction and fuel wood, mangroves are cleared extensively in swamps for channelization, rig and flow station construction, oil and gas pipe laying, and the establishment of human settlements which have all contributed immensely to the diminishing trend of mangrove vegetation in the region [39][40][41]. However, not forgetting the influence of coastal erosion, inundation and tidal wave action as a result of sea level rise (Fig. 10) ...
Article
This study assessed the effect of flood on fringe mangrove in South-eastern Nigeria. The approach includes assessing historical climatic factors of about 50 years in comparison to field studied data with the standard method of sampling and analysis. The mean temperature of surface water in south-eastern Nigeria ranges from 26.7°C to 32.0oC, salinity record varied from 17.7 0/00 to 31.7 0/00 minimum and maximum respectively, dissolved oxygen (DO) which indicates the healthy nature of a water body ranges between 3.7 and 5.0 mg/l. Mangroves coverage in the study area between 1982, 2003 and 2021 is given as 55%, 31% and 14% respectively, with ANOVA test p-value of 0.02 and 0.03 for row and column data. The correlation of temperature to rainfall show negative r = -0.09194, annual sea level show a strong correlation (r = 0.831499) with temperature, pointing out that temperature is the main key factor contributing to the flooding and inundation of the south-eastern Nigerian coast. Temperature and salinity correlate positively (r = 0.981) with each other and both correlate negatively with dissolved oxygen (r = -0.70, -0.82), correlate positively with mangrove species abundance (r = 0.838, 0.927) and diversity in same range while correlating negatively with mangrove evenness distribution (r = -2E-16). The study showed that the mangrove ecosystem in south-eastern Nigeria had decreased in size due to changing environmental condition such as temperature, salinity, annual rainfall and sea level rise. The goods and services provided by this ecosystem also decreased posing a threat to poverty alleviation and climate change mitigation in south-eastern Nigeria. The study concluded that aside from human influence to mangrove ecosystem, flood poses a great threat through inundation and coastal erosion to the survival and sustenance of this ecosystem and its services rendered to the environment and mankind in general.
... It is noteworthy that mangroves provide rich biodiversity and Carbon sink. Recommended measures for the mangrove forests are protection, restoration and reforestation [15]. ...
Article
Full-text available
The response to climate change depends on level of technology, socioeconomic factors and location. In this regard, interventions especially in developing countries may be different from the advance countries. This is more so as climate change interventions in developing countries will require economic empowerment to reduce poverty, promote food production and enhance nutrition. The human threat to climate change adaptation and mitigation in developing countries is not deliberate, but as means of daily livelihood and survival. In order to address the issues of climate change on sustainable bases, survival factors will be considered. In low technology environment as in Nigeria, natural climate solutions are top priority. The context of natural climate solutions is very wide and will depend on local conditions of well-being and environment. The Niger Delta of Nigeria is devastated by crude oil prospection/exploitation and climate change. It is agrarian and the vegetation is Rain and Mangrove Forests. The bulk of the Rain Forest has been degraded due to climate change leading to irreversible grassland called derived savannah, with severe socioeconomic consequences. The Mangrove Forest is devastated by climate change and the crude oil industry, with prospects of rehabilitation. In both cases, the natives are helpless and survival instinct leads to further degradation. The application of suitable natural climate solutions will address poverty and ensure sustainable forests. The objective of this paper was to present agro-based local intervention measures to enhance quality of life of the natives and ensure sustainable environment.
Article
Full-text available
This study focused on the application of the Systems Thinking System Dynamics (ST/SD) tool to analyse oil and gas environmental sustainability issues in the Niger Delta region (NDR) in Nigeria. Over the years, countries around the world have relied on oil and gas for energy security, economic growth, self-sufficiency and to gain geopolitical advantages. The exploration and production of oil and gas continue to be a priority in producer countries of the Global South with regulations being implemented to enhance the sustainability of the industry. In 2018, before the pandemic, global energy production was 14 421 Mtoe, an increase of 3.2% compared to 2017; mainly driven by coal, oil and gas. In total, fossil fuels accounted for up to 85% of global energy production the same year. Thus, despite the global sensitisation towards renewable energy, oil and gas continue to play a key role in shaping world economies. Globally, producing countries and oil and gas companies face the increasing demand to explain how they can contribute to the reduction of greenhouse gas emissions and the achievement of Paris Agreement goals. This has necessitated energy companies to carefully consider adapting their operations and business models to reduce the impacts on the environment. The study adopted Rentier State, Resource Curse and Stakeholder theories. This study adopted a qualitative approach, data was collected from secondary sources and analysed. To fully understand the issues in the NDR, the study employed the Systems Thinking System Dynamics (ST/SD) methodological tool to uncover the operational practices associated with oil and gas operations in the NDR. It is a holistic approach with elements of feedbacks and delays which enhance the understanding of a complex situation such as the NDR in Nigeria. Keywords: Environmental Sustainability, Oil and Gas Operations, Systems Thinking System Dynamics (ST/SD), Niger Delta Region (Nigeria). Proceedings Citation Format Rasaki T. James, Titus K. Olaniyi & Posi Olatubosun (2023): The Application of Systems Thinking System Dynamics (ST/SD) Tool to Analyse Oil and Gas Operations Environmental Sustainability Issues in the Niger Delta Region of Nigeria. Proceedings of the 37th iSTEAMS Multidisciplinary Cross-Border Conference. 30th October – 1st November, 2023. Academic City University College, Accra, Ghana. Pp 1-16. .dx.doi.org/10.22624/AIMS/ACCRACROSSBORDER2023V2P1
Article
Full-text available
The mangrove forest in Cross River State was assessed for information on its current plant species composition and density as well as trees stem-diameter distribution. Simple random sampling technique was used to select ten sample points on a gridded map of the mangrove forest. The ten selected sample points were located on the ground using their coordinates. At each sample point, one cluster consisting of five 20 m x 20 m nested plots laid alternately at 20 m intervals along a 200 m long transect was established. At the centre of each plot, a 2 m x 2 m quadrat was established as a nest. All living trees, shrubs and palms (with erect stems)  5cm in dbh were identified, counted and measured in the 20 m x 20 m plots, while trees' and palms' juveniles (<5cm in dbh), Acrostichum aureum, Nypa fruiticans fronds and their stumps were identified and counted in the 2 m x 2 m quadrats. The data were analysed using Microsoft Excel. A total of 22 plant species, belonging to 20 genera and 15 families were encountered in this study. These consisted of 15 species of trees, 2 species of shrubs, 4 species of palms and 1 species of ferns. Nypa fruticans was the most abundant species in the area. Total number of adult trees recorded was 547. Rhizophora racemosa (156), with a population density of 78 stems per hectare was the most abundant tree species. The stand structure showed an inverse J-shaped diameter distribution pattern.
Article
Full-text available
Dans la partie Nord du Grand Libreville, les quartiers Angondjé, Okala et Mikolongo connaissent une croissance démographique accompagnée d’une extension urbaine soutenue, et ayant des impacts sur les zones humides à mangroves. Considérée comme un danger écologique, la dégradation des mangroves dans ces milieux est due principalement aux activités anthropiques socio-économiques. Dans ces forêts à mangroves, les activités et les aménagements exercent des pressions humaines. La méthode de collecte des données et autres informations a fait appel respectivement, d’une part, sur le terrain à un guide d’observation directe et de caractérisation des activités socio-économiques, des prises de vues et l’utilisation d’un GPS et, d’autre part, la consultation des rapports divers et des documents cartographiques. Les données recueillies montrent que les activités tels que le bâti, le maraîchage, la pêche, la chasse et les manifestations de la pollution sont les facteurs de dégradation et déforestation des mangroves. Cette anthropisation problématique des milieux humides à mangroves se déroule dans un contexte d’étalement urbain favorisé par une urbanisation non maîtrisée, dans le nord du Grand Libreville. In the northern part of Greater Libreville, the Angondjé, Okala and Mikolongo districts are experiencing demographic growth accompanied by sustained urban expansion, and having impacts on wetlands with mangroves. Considered an ecological hazard, the degradation of mangroves in these environments is mainly due to anthropogenic socio-economic activities. In these mangrove forests, activities and developments exert human pressures. The method of collecting data and other information called respectively, on the one hand, on the ground for a guide of direct observation and characterization of socio-economic activities, shots and the use of a GPS and, on the other hand, the consultation of various reports and cartographic documents. The data collected show that activities such as construction, market gardening, fishing, hunting and manifestations of pollution are the factors of degradation and deforestation of mangroves. This problematic anthropization of wetlands with mangroves takes place in a context of urban sprawl favored by uncontrolled urbanization, in the north of Greater Libreville.
Article
This study examined species composition and occurrence pattern among mangroves across the Western Niger Delta. Vegetation measurements were carried out in one hundred quadrats of 20m by 20m. Rhizophora spp was dominant in Burutu, Opuama, Kurutie, Control (Importance Value Index =300, 177.28, 237.65, 300). A.germinans was dominant in Agge (IVI =183.03). Adult Rhizophora spp were dispersed in Agge, Burutu, Control (Morisita Index =0.25, 1.02, 0.025). Adult A. germinans were dispersed in Kurutie, Opuama, Agge (MI =0.07, 0.08, 0.26). Rhizophora spp juveniles were clustered in Agge, Burutu, Opuama, Kurutie, Control (MI =1.17, 1.86, 1.47, 1.9, 1.14). A. germinans juveniles were dispersed in Kurutie, Agge (MI =0.06, 0.69). Restoration and conservation programs should be established.
Article
Full-text available
Mangrove forests are one of the world's most threatened tropical ecosystems with global loss exceeding 35% (ref. 1). Juvenile coral reef fish often inhabit mangroves, but the importance of these nurseries to reef fish population dynamics has not been quantified. Indeed, mangroves might be expected to have negligible influence on reef fish communities: juvenile fish can inhabit alternative habitats and fish populations may be regulated by other limiting factors such as larval supply or fishing. Here we show that mangroves are unexpectedly important, serving as an intermediate nursery habitat that may increase the survivorship of young fish. Mangroves in the Caribbean strongly influence the community structure of fish on neighbouring coral reefs. In addition, the biomass of several commercially important species is more than doubled when adult habitat is connected to mangroves. The largest herbivorous fish in the Atlantic, Scarus guacamaia, has a functional dependency on mangroves and has suffered local extinction after mangrove removal. Current rates of mangrove deforestation are likely to have severe deleterious consequences for the ecosystem function, fisheries productivity and resilience of reefs. Conservation efforts should protect connected corridors of mangroves, seagrass beds and coral reefs.
Article
Full-text available
The latitudinal distribution of mangroves (Avicennia marina var. resinifera) in New Zealand has traditionally been considered to be controlled by climatic stress, particularly air temperature. This paper reviews the influence of climate factors, particularly frost, and the dispersal of mangrove propagules on the present-day mangrove distribution. There is no strong evidence to show that the southern limit of mangroves in New Zealand is a function of climatic conditions, or that the present mangrove distribution is in equilibrium with climatic conditions. It is probable that coastal processes affecting propagule dispersal are more important controls on the mangrove distribution within New Zealand than climatic factors. In particular, tidal asymmetry inhibits mixing of east and west coast mangrove populations around northern-most New Zealand, and low coastal current velocities and large distances between suitable habitats makes natural establishment south of present limits unlikely.
Article
Full-text available
Socio-economic surveys were carried out in the Malimba and Mouanko communities in the Sanaga delta region of the Douala-Edea Wildlife Reserve, Cameroon, on the exploitation, processing and marketing of bivalves, with emphasis on gender aspects and impacts on the surrounding forest resources. Sixty people from 16 villages were sampled using a structured questionnaire with field observations documented during the peak fishing period (November 2000–June 2001). Results indicated a strong gender differentiation in the activity, with males dominating bivalve harvesting and shell processing and women dominating the processing for meat. Monthly bivalve meat production of 32.9 tons (197.4 tons per year) generated revenues of 65.4 million FCFA (74.9 million per year). Monthly shell production was put at 1380 tons (8040 tons per year) generating a monthly revenue of 74 million FCFA (444 million per year). Problems faced during exploitation, processing and marketing stages include physical, health and socio-economic: use of very depreciable rudimentary tools, shell injuries, fire and hot water burns, insect pests; blindness, deafness; inadequate storage facilities, transport and remoteness of the area. Bivalve processing activities using wood contributed to a total annual harvest of 50 986 m3 from the surrounding forest. Sustainable conservation measures geared towards poverty alleviation are proposed.
Article
Full-text available
Mangrove forests occur along ocean coastlines throughout the tropics, and support numerous ecosystem services, including fisheries production and nutrient cycling. However, the areal extent of mangrove forests has declined by 30-50% over the past half century as a result of coastal development, aquaculture expansion and over-harvesting. Carbon emissions resulting from mangrove loss are uncertain, owing in part to a lack of broad-scale data on the amount of carbon stored in these ecosystems, particularly below ground. Here, we quantified whole-ecosystem carbon storage by measuring tree and dead wood biomass, soil carbon content, and soil depth in 25 mangrove forests across a broad area of the Indo-Pacific region--spanning 30° of latitude and 73° of longitude--where mangrove area and diversity are greatest. These data indicate that mangroves are among the most carbon-rich forests in the tropics, containing on average 1,023Mg carbon per hectare. Organic-rich soils ranged from 0.5m to more than 3m in depth and accounted for 49-98% of carbon storage in these systems. Combining our data with other published information, we estimate that mangrove deforestation generates emissions of 0.02-0.12Pg carbon per year--as much as around 10% of emissions from deforestation globally, despite accounting for just 0.7% of tropical forest area.
Article
Full-text available
Recent attention has focused on the high rates of annual carbon sequestration in vegetated coastal ecosystems-marshes, mangroves, and seagrasses-that may be lost with habitat destruction ('conversion'). Relatively unappreciated, however, is that conversion of these coastal ecosystems also impacts very large pools of previously-sequestered carbon. Residing mostly in sediments, this 'blue carbon' can be released to the atmosphere when these ecosystems are converted or degraded. Here we provide the first global estimates of this impact and evaluate its economic implications. Combining the best available data on global area, land-use conversion rates, and near-surface carbon stocks in each of the three ecosystems, using an uncertainty-propagation approach, we estimate that 0.15-1.02 Pg (billion tons) of carbon dioxide are being released annually, several times higher than previous estimates that account only for lost sequestration. These emissions are equivalent to 3-19% of those from deforestation globally, and result in economic damages of $US 6-42 billion annually. The largest sources of uncertainty in these estimates stems from limited certitude in global area and rates of land-use conversion, but research is also needed on the fates of ecosystem carbon upon conversion. Currently, carbon emissions from the conversion of vegetated coastal ecosystems are not included in emissions accounting or carbon market protocols, but this analysis suggests they may be disproportionally important to both. Although the relevant science supporting these initial estimates will need to be refined in coming years, it is clear that policies encouraging the sustainable management of coastal ecosystems could significantly reduce carbon emissions from the land-use sector, in addition to sustaining the well-recognized ecosystem services of coastal habitats.
Article
Full-text available
Recent research has highlighted the valuable role that coastal and marine ecosystems play in sequestering carbon dioxide (CO2). The carbon (C) sequestered in vegetated coastal ecosystems, specifically mangrove forests, seagrass beds, and salt marshes, has been termed "blue carbon". Although their global area is one to two orders of magnitude smaller than that of terrestrial forests, the contribution of vegetated coastal habitats per unit area to long-term C sequestration is much greater, in part because of their efficiency in trapping suspended matter and associated organic C during tidal inundation. Despite the value of mangrove forests, seagrass beds, and salt marshes in sequestering C, and the other goods and services they provide, these systems are being lost at critical rates and action is urgently needed to prevent further degradation and loss. Recognition of the C sequestration value of vegetated coastal ecosystems provides a strong argument for their protection and restoration; however, it is necessary to improve scientific understanding of the underlying mechanisms that control C sequestration in these ecosystems. Here, we identify key areas of uncertainty and specific actions needed to address them.