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Weekly Wetland
Sustainability Report
Volume 1 Issue 11 Weekly Wetland Sustainability Report 16 September 2019
Inside This IssueAnnouncement
Editor
Fadeke Ayoola
In this issue, we focus on coastal
natural capital.
How do we counteract coastal erosion,
wetland depletion and environmental
degradation to improve economic
growth? We look at different regions
within Africa to understand how they
are addressing the challenges of
managing coastal natural capital, as
well as the potential solutions to the
issue, soft and hard coastal
management techniques.
Volume 1 Issue 9 Weekly Wetland Sustainability Report 16 September 2019 Page 1
Image courtesy of Blue Planet Oceans and Society
1. CASE STUDY 1: Mangrove Ecosystem
Economic Value in Mida Creek, Kenya.
Discussing the link between coastal
natural capital and sustainable
economic growth. Discussing
economic value of mangrove ecosystem
provisioning services, regulating and
supporting services and recreational
services. We also discuss Kenya’s
mangrove ecosystem management plan
2017 to 2027.
2. CASE STUDY 2: West, Central & Southern
Africa challenges in eco-governance.
Anthropogenic causes of coastal erosion
in West, Central & Southern African
region. Soft and hard techniques to
address coastal erosion.
Coastal Natural Capital
How do we counteract coastal erosion, wetland depletion and
environmental degradation to improve economic growth?
2
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91% Fish - Value
US$ 735,800
5% Firewood &
Charcoal - Value US$
45,500
2% Raw Construction Materials -
Value US$ 13,200
2% Honey - value US$ 14,700
Chart 1: Total Economic Value of
mangrove ecosystem
Provisioning services
Fish
Firewood & Charcoal
Raw Construction
Materials
Honey
2% Biodiversity,
value US$ 129,000
56% Shoreline
protection, value
US$ 2,914,000
6% Carbon sequestration,
value US$ 293,400
36% Fish breeding & nursery,
value US$ 1,873,000
Chart Title Biodiversity
Shoreline protection
Carbon sequestration
Fish breeding &
nursery
Link between coastal natural capital and sustainable economic growth By Fadeke Ayoola
Chart 1: Economic value of Mangrove Ecosystem Provisioning Services – Kenya (MIDA CREEK)
CASE STUDY 1: Mangrove Ecosystem Economic Value in Mida Creek, Kenya
The relationship between economic growth and coastal natural capital is still an emerging field. Coastal natural capital
provides essential goods and ecosystem services such as food, energy, construction materials for the population. Habitat
and food for wildlife. Jobs, tourism and investment for the economy, as well as acting as a form of mitigation against
emissions and waste. Coastal natural capital are essential inputs for production, for example, Chart 1- 3 show the outcome
of a study conducted by the Food and Agricultural Organization (FAO), to understand the economic value of mangroves in
Mida Creek in Kenya. Mida Creek Mangroves form part of the coastal natural capital in Kenya, there are many other natural
capital assets within this Creek, but Mangroves is the focus of this study. Mida Creek is a broad water tidal creek surrounded
by extensive mangroves and lined with palms. Wildlife benefit extensively from Mida Creek, for example, a wide variety of
aquatic species live in the roots of the mangrove, migratory birds use the Creek often as a stopover on flight to other
destinations and Flamingos can often be seen feeding in the Mida. The economic value of the Mida Creek divided into
three economic valuation services, provisioning, regulatory, supporting services, and recreational services.
The total value of provisioning services provide by mangroves is US$ 809,200.
Chart 2: Economic value of Mangrove Ecosystem Regulating & Supporting Services – Kenya (MIDA CREEK)
Source: Data by FAO
Chart 1, above shows the results for provisioning services provided by the mangroves within Mida Creek. There are four
types of assets providing economic benefit from the provisional services of mangroves. Fish, representing 91% of
provisioning services valued at US$ 735,800. Firewood and charcoal valued at US$ 45,500, honey valued at US$ 14,700
and raw construction materials US$ 13,200. These provisional services contribute towards the economic growth of the
country. Therefore, the coastal management of mangroves are vitally important for not only the population and wildlife but
for the sustainability of the economy.
Chart 2: Economic value of Mangrove Ecosystem Regulating and Supporting Services – Kenya (MIDA
CREEK)
Source: Data by FAO
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Link between coastal natural capital and sustainable economic growth By Fadeke Ayoola
Chart 2, shows the results for regulating and supporting services provided by the mangroves within Mida Creek.
There are four types of assets providing economic benefit from the regulating and supporting services of mangroves.
Notably, shoreline protection valued at US$ 2,914,000 and fish breeding and nursery valued at US$ 1,873,000. Clearly, the
environmental management and eco-governance of these coastal capital assets are critical for sustainable economic growth
and the wellbeing of the country. The ministry of environment, natural resources and regional development authorities in
Kenya are responsible for the eco-management and governance of mangroves. The ministry of the environment in Kenya
understand the root causes of mangrove loss. Mangrove losses identified as; increased population, weak governance,
inadequate awareness of the true value of mangrove ecosystems, high levels of poverty, lack of alternative livelihoods, and
inadequate management prescriptions. In response to the root causes of mangrove loss, the Kenyan environment agency
has implemented the Mangrove ecosystem management plan 2017 to 2027. Below, in table 1, a summary of the main
threats caused by human-induced threats and natural threats.
Table 1: Threats to mangroves in Kenya (Including Mida Creek)
Human-induced threats Natural threats
Over-exploitation of wood products Heavy Rainfall
Conversion of mangrove areas to other land uses Pest infestation and desiccation
Aquaculture Sea-level rises
Pollution and sedimentation
Diversion and damming of rivers
Infrastructure and development
To address issues summarized in table 1, the Kenyan authorities have set out within the Mangrove ecosystem management
plan the agenda to identify and map out mangrove areas with unique habitats and species for biodiversity conservation.
Chart 3, above shows the results for recreational services provided by the mangroves within Mida Creek. There are two
types of assets providing economic benefit from the recreational services of mangroves. Notably, tourism and recreation
valued at US$ 497,500 and education and research valued at US$ 44,000.
This case study has clearly identified the importance of coastal natural capital and the contribution it makes to the economic
growth of Kenya.
In Chart 4, below we see the real GDP growth rate in Africa, from 2010 to 2020. During the period 2010 to 2014, the West
African region leading in economic growth, followed by the East African region, Central, North and finally South Africa.
However, in the years following the West, Central and South African regions show decline in economic growth. The link
between economic losses and environmental degradation could partially explain these results.
8% Education & Research
value US$ 44,000
92% Tourism & recreation
value US$ 497,500
Education &
research
Tourism &
recreation
Chart 3: Economic value of Mangrove Ecosystem Recreational Services – Kenya (MIDA CREEK)
Source: Data by FAO
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Diagram 1: Anthropogenic causes of coastal erosion in West, Central & Southern African region
5.9
3.7
6.2 5 3.8
6.5
3.7
3.2 3.3
1.6
5.1
3.2 0.5
0.2
0.7
5.9
4.9
2.7
1.1
1.6
5.7
4.3
3.3
2.2
1.2
5.9
4.4
3.6
3.6
2.2
6.1
4.3
3.6
3.5
2.8
East Africa north Africa West Africa Central Africa South Africa
CHART 4: REAL GDP GROWTH IN AFRICA, 2010-20
2010-2014 2015 2016 2017 2018 2019 2020
Anthropogenic causes
of coastal erosion and
Wetland depletion
Land reclamation
Environmental Impact: - disruption of the
ocean’s ecosystem, water pollution,
deforestation, mangrove and coral reefs
deterioration.
Vegetation Clearing
Oil and Gas mining
Dredging
Ship-induced waves
Carbon emission
River damming
Harbour infrastructure
Environmental Impact: -
Changing ecosystem services
and harming human health.
Environmental Impact: -
Erosion of coastal deltas,
extinction of fish and other
aquatic species, disappearance
of birds, loss of forest.
Environmental Impact: - harming
coral reefs and fish nurseries,
destroying seagrasses.
Environmental Impact: - abandoned
and degraded coastal wetlands emit high
volumes of carbon dioxide directly into the
atmosphere contributing to climate change.
Environmental Impact: - Discharges
through leaks, spillages, and cargo
vapour emissions.
Environmental Impact: -
destroying wildlife habitat,
defenceless against wind
erosion, beach erosion.
Environmental Impact: -
Leaks and oil spills can cause
depletion of aquatic wild life,
birds, and fish. Destroying
ecosystem.
GDP Growth rates for 2019 and 2020 predicted.
Real GDP Growth in Africa, 2010-2020 By Fadeke Ayoola
Source: African Development Bank
CASE STUDY 2: West, Central & Southern African challenges
According to the World Bank, coastal natural capital assets is the source of 56 percent of West Africa’s GDP. That is over half
of the region’s economic growth is attributed to coastal natural capital. Yet, coastal natural capital assets, particularly within the
Niger Delta region, from fisheries to mangroves face significant threats from anthropogenic interventions and the potential
impacts of climate change. Chart 4, above shows the decline in economic growth for the West, Central and Southern African
region, which can be partially attributed to the degradation of coastal natural capital assets.
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TABLE 1: SOFT TECHNIQUES TO ADDRESS COASTAL EROSION
Source: National Institute of Coastal and Marine Management of the Netherlands
TECHNIQUES PRINCIPLES LIMITATION OF APPLICATION
Artificial reef
creation
Building an artificial reef which absorbs the wave
energy (thus providing coastal defence), while
providing a natural habitat for marine biodiversity and
opportunities for recreational activities.
Only a few examples of artificial reef creation exist in
Europe (in Sea Palling, UK mainly), but seems to
provide good results.
Beach drainage
Beach drainage decreases the volume of surface
water during backwash by allowing water to percolate
into the beach, thus reducing the seaward movement
of sediment. Beach drainage also leads to drier and
“gold” coloured sand, more appreciated for
recreational activities.
The technique is relatively new and experience lacks
to assess its performance. However, beach drainage
is adapted when erosion mainly occurs cross-shore)
(non-significant long-shore drift).
Sand supply or
Nourishment
Artificial increase of sand volumes in the foreshore via
the supply of exogenous sand. Sand supply may be
achieved through the direct placement of sediment on
the beach, through trickle charging (placing sediments
at a single point), or through pumping. It can also take
place in the emerged part of the beach nourishment
or under the waterline, which is generally cheaper.
Beach and underwater nourishment have been very
popular in the North because of the availability of
sediments, which has similar properties as the beach
sediment. When sediment is not available and has to
be imported from another region, beach nourishment
may not be the best decision. Nourishment schemes
have also carefully designed as they may alter the
biota (both on the beach and in the dredging area).
Beach scraping Artificial re-profiling of the beach when sediment
losses are not severe enough to warrant the
importation of large volumes of sediments. Re-
profiling achieved using existing beach sediment.
Beach scraping is among the cheapest techniques, as
it does not require importing sand. However, the
process carried out several times before finding the
right profile. It is also restricted to those beaches where
cross-shore erosion is dominant and storms not heavy.
Cliff drainage Reduction of pore pressure by piping water out of the
cliff and therefore preventing the accumulation of
water at rock boundaries.
May not be applicable for all types of cliffs.
Cliff profiling Change of cliff faces angle to increase cliff stability. The
angle at which cliff become stable is a function of rock
type, geologic structure, and water content.
May not be applicable for all types of cliffs, and the
techniques require a good knowledge of the cliff geologic
structure and watering process.
Cliff toe protection Protection of the cliff base by placing blocks at the foot
of the potential failure surface.
This technique is easy to achieve but do not stop erosion
completely. It may therefore be adapted in the case
where there is further loss of lands is still acceptable.
Creation of stable
bays
Increasing the length of the coastline to dilute wave
energy per unit length of the coast. While some coastline
segments protected, erosion continues between these
hard-points leading to the formation of embayment.
This technique rarely used in Africa.
Dune regeneration Wind-blown accumulation of drifted sand located in the
supra-tidal zone. Wind velocity reduced by way of
porous fences made of wood, geo-textile, plants, which
encourages sand deposition.
Adapted for those cases where the wind plays an
important role.
Soft techniques to address coastal erosion in West, Central & Southern African region by Fadeke Ayoola
By Fadeke Ayoola
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TABLE 2: HARD TECHNIQUES TO ADDRESS COASTAL EROSION
TECHNIQUES PRINCIPLES LIMIT OF APPLICATION
Breakwater Breakwaters are protective structures placed offshore,
generally in hard materials such as concrete or rocks,
which aim at absorbing the wave energy before the
waves reach the shore.
Breakwaters reflect or diffract wave energy in destructive
ways or concentrate it in local hot spots. Erosion problems
and the scouring effects of misdirected energy lead to the
loss of beach/coastline and undermine the protected
structures.
Gabion The gabion is a metal cage filled with rocks, about 1
metre by 1 metre square. Gabions are stacked to form
a simple wall.
Used to protect a cliff area in the short term only. Can be
easily damaged by powerful storm waves and the cages
tend to rust quite quickly. Gabions have the advantage of the
ease of use and are relatively cheap but their life span is
short.
Geotextiles Geotextiles are permeable fabrics, which are able to
hold back materials while water flows through.
Geosynthetic tubes are large tubes consisting of a
woven geotextile material filled with a slurry-mix. The
mix usually consists of dredged material (e.g. sand)
from the nearby area but can also be a mortar or
concrete mix.
Geotextiles are relatively new in application.
Groin fields Groins are structures that extend perpendicularly from
the shore. Usually constructed in groups called groin
fields, their purpose is to trap and retain sand,
nourishing the beach compartments between them.
Groins may be made of wooden or rocky materials.
They interrupt the longshore transport of littoral drift.
When a well-designed groin field fills to capacity with
sand, longshore transport continues at about the same
rate as before. Once the groins built, a stable beach
maintained.
Sand accumulated between groins contributes to a sediment
deficit down-drift. Coastal erosion problems shifted to other
locations. Thus, to be effective, groins should be limited to
those cases where longshore transport is predominantly in
one direction, and where their activities will not cause
unacceptable erosion of the down drift shore.
Revetments The revetment is a sloping feature, which breaks up or
absorbs the energy of the waves but may let water and
sediment pass through. The older wooden revetment
consists of posts fixed into the beach with wooden slats
between. Modern revetments have concrete or shaped
blocks of stone laid on top of a layer of finer material.
Rock armour or riprap consists of layers of very hard
rock with the largest, often weighing several tonnes, on
the top. Riprap has the advantage of good permeability
and looks more natural.
Revetments are adapted to the foreshore with a gentle
slope. It has the same adverse effect as seawalls though
with reduced intensity. It also results in changing the nature
of the sea frontage, which may lead to further changes in the
foreshore ecosystems.
Seawall Bulkheads and seawalls protect banks and bluffs by
completely separating land from water. Bulkheads act
as retaining walls, keeping the earth or sand behind
them from crumbling or slumping. Seawalls are primarily
used to resist wave action. Design considerations for
these types of structures are similar. These structures
do not protect the shore in front of them, however.
When bulkheads and seawalls are used in areas where
there is significant wave action, they may accelerate beach
erosion (much of the energy of the waves breaking on the
structure is redirected downward to the toe). Bulkheads and
seawalls are most appropriate where fishing and boating are
the primary uses of the shore, and gently sloping areas for
sunbathing or shallow-water swimming are not essential.
They are also critical when risks associated with coastal
erosion are imminent.
Source: National Institute of Coastal and Marine Management of the Netherlands
Hard techniques to address coastal erosion in West Africa and beyond By Fadeke Ayoola

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  • 1. 1 C2 General Weekly Wetland Sustainability Report Volume 1 Issue 11 Weekly Wetland Sustainability Report 16 September 2019 Inside This IssueAnnouncement Editor Fadeke Ayoola In this issue, we focus on coastal natural capital. How do we counteract coastal erosion, wetland depletion and environmental degradation to improve economic growth? We look at different regions within Africa to understand how they are addressing the challenges of managing coastal natural capital, as well as the potential solutions to the issue, soft and hard coastal management techniques. Volume 1 Issue 9 Weekly Wetland Sustainability Report 16 September 2019 Page 1 Image courtesy of Blue Planet Oceans and Society 1. CASE STUDY 1: Mangrove Ecosystem Economic Value in Mida Creek, Kenya. Discussing the link between coastal natural capital and sustainable economic growth. Discussing economic value of mangrove ecosystem provisioning services, regulating and supporting services and recreational services. We also discuss Kenya’s mangrove ecosystem management plan 2017 to 2027. 2. CASE STUDY 2: West, Central & Southern Africa challenges in eco-governance. Anthropogenic causes of coastal erosion in West, Central & Southern African region. Soft and hard techniques to address coastal erosion. Coastal Natural Capital How do we counteract coastal erosion, wetland depletion and environmental degradation to improve economic growth?
  • 2. 2 C2 General 91% Fish - Value US$ 735,800 5% Firewood & Charcoal - Value US$ 45,500 2% Raw Construction Materials - Value US$ 13,200 2% Honey - value US$ 14,700 Chart 1: Total Economic Value of mangrove ecosystem Provisioning services Fish Firewood & Charcoal Raw Construction Materials Honey 2% Biodiversity, value US$ 129,000 56% Shoreline protection, value US$ 2,914,000 6% Carbon sequestration, value US$ 293,400 36% Fish breeding & nursery, value US$ 1,873,000 Chart Title Biodiversity Shoreline protection Carbon sequestration Fish breeding & nursery Link between coastal natural capital and sustainable economic growth By Fadeke Ayoola Chart 1: Economic value of Mangrove Ecosystem Provisioning Services – Kenya (MIDA CREEK) CASE STUDY 1: Mangrove Ecosystem Economic Value in Mida Creek, Kenya The relationship between economic growth and coastal natural capital is still an emerging field. Coastal natural capital provides essential goods and ecosystem services such as food, energy, construction materials for the population. Habitat and food for wildlife. Jobs, tourism and investment for the economy, as well as acting as a form of mitigation against emissions and waste. Coastal natural capital are essential inputs for production, for example, Chart 1- 3 show the outcome of a study conducted by the Food and Agricultural Organization (FAO), to understand the economic value of mangroves in Mida Creek in Kenya. Mida Creek Mangroves form part of the coastal natural capital in Kenya, there are many other natural capital assets within this Creek, but Mangroves is the focus of this study. Mida Creek is a broad water tidal creek surrounded by extensive mangroves and lined with palms. Wildlife benefit extensively from Mida Creek, for example, a wide variety of aquatic species live in the roots of the mangrove, migratory birds use the Creek often as a stopover on flight to other destinations and Flamingos can often be seen feeding in the Mida. The economic value of the Mida Creek divided into three economic valuation services, provisioning, regulatory, supporting services, and recreational services. The total value of provisioning services provide by mangroves is US$ 809,200. Chart 2: Economic value of Mangrove Ecosystem Regulating & Supporting Services – Kenya (MIDA CREEK) Source: Data by FAO Chart 1, above shows the results for provisioning services provided by the mangroves within Mida Creek. There are four types of assets providing economic benefit from the provisional services of mangroves. Fish, representing 91% of provisioning services valued at US$ 735,800. Firewood and charcoal valued at US$ 45,500, honey valued at US$ 14,700 and raw construction materials US$ 13,200. These provisional services contribute towards the economic growth of the country. Therefore, the coastal management of mangroves are vitally important for not only the population and wildlife but for the sustainability of the economy. Chart 2: Economic value of Mangrove Ecosystem Regulating and Supporting Services – Kenya (MIDA CREEK) Source: Data by FAO
  • 3. 3 C2 General Link between coastal natural capital and sustainable economic growth By Fadeke Ayoola Chart 2, shows the results for regulating and supporting services provided by the mangroves within Mida Creek. There are four types of assets providing economic benefit from the regulating and supporting services of mangroves. Notably, shoreline protection valued at US$ 2,914,000 and fish breeding and nursery valued at US$ 1,873,000. Clearly, the environmental management and eco-governance of these coastal capital assets are critical for sustainable economic growth and the wellbeing of the country. The ministry of environment, natural resources and regional development authorities in Kenya are responsible for the eco-management and governance of mangroves. The ministry of the environment in Kenya understand the root causes of mangrove loss. Mangrove losses identified as; increased population, weak governance, inadequate awareness of the true value of mangrove ecosystems, high levels of poverty, lack of alternative livelihoods, and inadequate management prescriptions. In response to the root causes of mangrove loss, the Kenyan environment agency has implemented the Mangrove ecosystem management plan 2017 to 2027. Below, in table 1, a summary of the main threats caused by human-induced threats and natural threats. Table 1: Threats to mangroves in Kenya (Including Mida Creek) Human-induced threats Natural threats Over-exploitation of wood products Heavy Rainfall Conversion of mangrove areas to other land uses Pest infestation and desiccation Aquaculture Sea-level rises Pollution and sedimentation Diversion and damming of rivers Infrastructure and development To address issues summarized in table 1, the Kenyan authorities have set out within the Mangrove ecosystem management plan the agenda to identify and map out mangrove areas with unique habitats and species for biodiversity conservation. Chart 3, above shows the results for recreational services provided by the mangroves within Mida Creek. There are two types of assets providing economic benefit from the recreational services of mangroves. Notably, tourism and recreation valued at US$ 497,500 and education and research valued at US$ 44,000. This case study has clearly identified the importance of coastal natural capital and the contribution it makes to the economic growth of Kenya. In Chart 4, below we see the real GDP growth rate in Africa, from 2010 to 2020. During the period 2010 to 2014, the West African region leading in economic growth, followed by the East African region, Central, North and finally South Africa. However, in the years following the West, Central and South African regions show decline in economic growth. The link between economic losses and environmental degradation could partially explain these results. 8% Education & Research value US$ 44,000 92% Tourism & recreation value US$ 497,500 Education & research Tourism & recreation Chart 3: Economic value of Mangrove Ecosystem Recreational Services – Kenya (MIDA CREEK) Source: Data by FAO
  • 4. 4 C2 General Diagram 1: Anthropogenic causes of coastal erosion in West, Central & Southern African region 5.9 3.7 6.2 5 3.8 6.5 3.7 3.2 3.3 1.6 5.1 3.2 0.5 0.2 0.7 5.9 4.9 2.7 1.1 1.6 5.7 4.3 3.3 2.2 1.2 5.9 4.4 3.6 3.6 2.2 6.1 4.3 3.6 3.5 2.8 East Africa north Africa West Africa Central Africa South Africa CHART 4: REAL GDP GROWTH IN AFRICA, 2010-20 2010-2014 2015 2016 2017 2018 2019 2020 Anthropogenic causes of coastal erosion and Wetland depletion Land reclamation Environmental Impact: - disruption of the ocean’s ecosystem, water pollution, deforestation, mangrove and coral reefs deterioration. Vegetation Clearing Oil and Gas mining Dredging Ship-induced waves Carbon emission River damming Harbour infrastructure Environmental Impact: - Changing ecosystem services and harming human health. Environmental Impact: - Erosion of coastal deltas, extinction of fish and other aquatic species, disappearance of birds, loss of forest. Environmental Impact: - harming coral reefs and fish nurseries, destroying seagrasses. Environmental Impact: - abandoned and degraded coastal wetlands emit high volumes of carbon dioxide directly into the atmosphere contributing to climate change. Environmental Impact: - Discharges through leaks, spillages, and cargo vapour emissions. Environmental Impact: - destroying wildlife habitat, defenceless against wind erosion, beach erosion. Environmental Impact: - Leaks and oil spills can cause depletion of aquatic wild life, birds, and fish. Destroying ecosystem. GDP Growth rates for 2019 and 2020 predicted. Real GDP Growth in Africa, 2010-2020 By Fadeke Ayoola Source: African Development Bank CASE STUDY 2: West, Central & Southern African challenges According to the World Bank, coastal natural capital assets is the source of 56 percent of West Africa’s GDP. That is over half of the region’s economic growth is attributed to coastal natural capital. Yet, coastal natural capital assets, particularly within the Niger Delta region, from fisheries to mangroves face significant threats from anthropogenic interventions and the potential impacts of climate change. Chart 4, above shows the decline in economic growth for the West, Central and Southern African region, which can be partially attributed to the degradation of coastal natural capital assets.
  • 5. 5 C2 General TABLE 1: SOFT TECHNIQUES TO ADDRESS COASTAL EROSION Source: National Institute of Coastal and Marine Management of the Netherlands TECHNIQUES PRINCIPLES LIMITATION OF APPLICATION Artificial reef creation Building an artificial reef which absorbs the wave energy (thus providing coastal defence), while providing a natural habitat for marine biodiversity and opportunities for recreational activities. Only a few examples of artificial reef creation exist in Europe (in Sea Palling, UK mainly), but seems to provide good results. Beach drainage Beach drainage decreases the volume of surface water during backwash by allowing water to percolate into the beach, thus reducing the seaward movement of sediment. Beach drainage also leads to drier and “gold” coloured sand, more appreciated for recreational activities. The technique is relatively new and experience lacks to assess its performance. However, beach drainage is adapted when erosion mainly occurs cross-shore) (non-significant long-shore drift). Sand supply or Nourishment Artificial increase of sand volumes in the foreshore via the supply of exogenous sand. Sand supply may be achieved through the direct placement of sediment on the beach, through trickle charging (placing sediments at a single point), or through pumping. It can also take place in the emerged part of the beach nourishment or under the waterline, which is generally cheaper. Beach and underwater nourishment have been very popular in the North because of the availability of sediments, which has similar properties as the beach sediment. When sediment is not available and has to be imported from another region, beach nourishment may not be the best decision. Nourishment schemes have also carefully designed as they may alter the biota (both on the beach and in the dredging area). Beach scraping Artificial re-profiling of the beach when sediment losses are not severe enough to warrant the importation of large volumes of sediments. Re- profiling achieved using existing beach sediment. Beach scraping is among the cheapest techniques, as it does not require importing sand. However, the process carried out several times before finding the right profile. It is also restricted to those beaches where cross-shore erosion is dominant and storms not heavy. Cliff drainage Reduction of pore pressure by piping water out of the cliff and therefore preventing the accumulation of water at rock boundaries. May not be applicable for all types of cliffs. Cliff profiling Change of cliff faces angle to increase cliff stability. The angle at which cliff become stable is a function of rock type, geologic structure, and water content. May not be applicable for all types of cliffs, and the techniques require a good knowledge of the cliff geologic structure and watering process. Cliff toe protection Protection of the cliff base by placing blocks at the foot of the potential failure surface. This technique is easy to achieve but do not stop erosion completely. It may therefore be adapted in the case where there is further loss of lands is still acceptable. Creation of stable bays Increasing the length of the coastline to dilute wave energy per unit length of the coast. While some coastline segments protected, erosion continues between these hard-points leading to the formation of embayment. This technique rarely used in Africa. Dune regeneration Wind-blown accumulation of drifted sand located in the supra-tidal zone. Wind velocity reduced by way of porous fences made of wood, geo-textile, plants, which encourages sand deposition. Adapted for those cases where the wind plays an important role. Soft techniques to address coastal erosion in West, Central & Southern African region by Fadeke Ayoola By Fadeke Ayoola
  • 6. 6 C2 General TABLE 2: HARD TECHNIQUES TO ADDRESS COASTAL EROSION TECHNIQUES PRINCIPLES LIMIT OF APPLICATION Breakwater Breakwaters are protective structures placed offshore, generally in hard materials such as concrete or rocks, which aim at absorbing the wave energy before the waves reach the shore. Breakwaters reflect or diffract wave energy in destructive ways or concentrate it in local hot spots. Erosion problems and the scouring effects of misdirected energy lead to the loss of beach/coastline and undermine the protected structures. Gabion The gabion is a metal cage filled with rocks, about 1 metre by 1 metre square. Gabions are stacked to form a simple wall. Used to protect a cliff area in the short term only. Can be easily damaged by powerful storm waves and the cages tend to rust quite quickly. Gabions have the advantage of the ease of use and are relatively cheap but their life span is short. Geotextiles Geotextiles are permeable fabrics, which are able to hold back materials while water flows through. Geosynthetic tubes are large tubes consisting of a woven geotextile material filled with a slurry-mix. The mix usually consists of dredged material (e.g. sand) from the nearby area but can also be a mortar or concrete mix. Geotextiles are relatively new in application. Groin fields Groins are structures that extend perpendicularly from the shore. Usually constructed in groups called groin fields, their purpose is to trap and retain sand, nourishing the beach compartments between them. Groins may be made of wooden or rocky materials. They interrupt the longshore transport of littoral drift. When a well-designed groin field fills to capacity with sand, longshore transport continues at about the same rate as before. Once the groins built, a stable beach maintained. Sand accumulated between groins contributes to a sediment deficit down-drift. Coastal erosion problems shifted to other locations. Thus, to be effective, groins should be limited to those cases where longshore transport is predominantly in one direction, and where their activities will not cause unacceptable erosion of the down drift shore. Revetments The revetment is a sloping feature, which breaks up or absorbs the energy of the waves but may let water and sediment pass through. The older wooden revetment consists of posts fixed into the beach with wooden slats between. Modern revetments have concrete or shaped blocks of stone laid on top of a layer of finer material. Rock armour or riprap consists of layers of very hard rock with the largest, often weighing several tonnes, on the top. Riprap has the advantage of good permeability and looks more natural. Revetments are adapted to the foreshore with a gentle slope. It has the same adverse effect as seawalls though with reduced intensity. It also results in changing the nature of the sea frontage, which may lead to further changes in the foreshore ecosystems. Seawall Bulkheads and seawalls protect banks and bluffs by completely separating land from water. Bulkheads act as retaining walls, keeping the earth or sand behind them from crumbling or slumping. Seawalls are primarily used to resist wave action. Design considerations for these types of structures are similar. These structures do not protect the shore in front of them, however. When bulkheads and seawalls are used in areas where there is significant wave action, they may accelerate beach erosion (much of the energy of the waves breaking on the structure is redirected downward to the toe). Bulkheads and seawalls are most appropriate where fishing and boating are the primary uses of the shore, and gently sloping areas for sunbathing or shallow-water swimming are not essential. They are also critical when risks associated with coastal erosion are imminent. Source: National Institute of Coastal and Marine Management of the Netherlands Hard techniques to address coastal erosion in West Africa and beyond By Fadeke Ayoola