How effective were mangroves as a defence against the recent tsunami?
Dahdouh-Guebas 2005 Current Biology
Magazine
R443
substrates depend on binding at
Essay
this site, there are probably
additional substrate recognition
sites. Another contribution to
How effective were mangroves as a
substrate selection is made by
scaffold proteins, e.g. AKAP79,
defence against the recent tsunami?
which target the phosphatase to
neuronal synapses or other
cellular sites. Calcineurin also Whether or not mangroves function as buffers against tsunamis is the
delegates work to protein subject of in-depth research, the importance of which has been
phosphatase 1 (PP1) through a neglected or underestimated before the recent killer tsunami struck. Our
phosphatase cascade, in which preliminary post-tsunami surveys of Sri Lankan mangrove sites with
dephosphorylation of the PP1 different degrees of degradation indicate that human activity
antagonists DARPP-32 or exacerbated the damage inflicted on the coastal zone by the tsunami.
inhibitor-1 by calcineurin relieves
their inhibitory effect on PP1, and
F. Dahdouh-Guebas1*,
allows PP1 to act on its own their large above-ground aerial
L.P. Jayatissa3*, D. Di Nitto1,
preferred substrates. root systems and standing crop.
J.O. Bosire4, D. Lo Seen5 and Like many habitats, mangrove
N. Koedam2
What are its inhibitors? forests have been degraded and
Cyclosporin A (CsA) and FK506 destroyed by humans, and their
bind tightly to the abundant Mangrove forests have iconic loss is a source of global concern.
In the second half of the 20th
intracellular proteins cyclophilin A status as natural ecosystems that
and FKBP12, respectively, and provide services to humans. They century, 50% of the world’s
the resulting ligand–protein function as breeding, spawning, mangrove forests have been
complex binds to calcineurin and hatching and nursing grounds for destroyed, and current annual
impedes access of protein marine and pelagic species, and loss rates vary from 1 to 20% [1].
substrates to the active site. are important in the daily Ironically, the great human
Blockade of a biological process livelihood of local human tragedy of the recent December
26th tsunami may provide the
by CsA and independently by subsistence communities.
FK506 is diagnostic for Mangrove representatives such as stimulus for a better
calcineurin involvement. Other Rhizophora spp. also function as a understanding of what mangrove
inhibitors that find frequent physical barrier against tidal and forests can and cannot do for
experimental use are the ocean influences by means of human well-being.
autoinhibitory peptide from
calcineurin and fragments of the 6. Walawey Ganga E.
8. Kahandamodara L.
regulatory proteins Relatively good pre-tsunami 9. Rekawa L.
mangrove status 11. Dickwella
DSCR1/MCIP/calcipressin/Rcn1p, 12. Talalla L.
Cryptic
Cabin1/cain, and AKAP79. 20. Akurala
ecological
18. Galle-Unawatuna
degradation
17. Koggala L.
Does it have any medical 21. Balapitiya E.
1. Batticaloa L.
relevance? Calcineurin signalling 7. Kalametiya L.
is prominent in transplant 13. Devinuwara L.
Bad pre-tsunami 14. Nilwala Ganga E.
rejection and autoimmune mangrove status 15. Polwatumodara
16. Kapparatota
disease, where the inhibitors CsA
19. Ginganga E.
and FK506 are used clinically, and 4. Palatupana L.
5. Kirinda L.
is being studied for its No 9. Kirama Oya mouth
contribution to myocardial cryptic 22. Kosgoda
ecological 23. Bentota Ganga E.
hypertrophy and to virulence in degradation
24. Kaluwamodara
fungal pathogens. 2. Komari L.
Relatively good pre-tsunami
3. Pottuvil L.
mangrove status
100
90
80
70
60
Where can I find out more? Similarity Current Biology
Aramburu, J., Rao, A., and Klee, C.B.
(2000). Calcineurin: from structure
Figure 1. Dendrogram generated by a cluster analysis of the 24 mangrove sites
to function. Curr. Top. Cell. Regul.
investigated, indicating their characteristics and the impact of the tsunami (big wave,
36, 237–295.
severely impacted; small wave, little impacted).
Rusnak, F., and Mertz, P. (2000).
Calcineurin: form and function. The ‘mangrove status’ is a combination of pre-tsunami aerial extent of the front man-
Physiol. Rev. 80, 1483–1521. grove and pre-tsunami mangrove destruction (see text). The tsunami had only a small
impact on lagoons that show no cryptic ecological degradation (sites 2, 3, 23 and 24)
or that are protected by the distance from the shore and by frontal Rhizophora spp.
fringes (sites 17, 18 and 21). The lagoons are numbered clockwise from East to West,
The CBR Institute for Biomedical
to emphasize that damage was not linked to geographic position in view of tsunami
Research and Department of Pathology,
wave energy. A map overview of all lagoons can be found in Jayatissa et al. [18], with
Harvard Medical School, Boston,
the exception of Batticaloa, Komari and Potuvil, which are located at the easternmost
Massachusetts 02115, USA.
extremity of the island. L, Lagoon; E, Estuary.
E-mail: hogan@cbr.med.harvard.edu
Current Biology Vol 15 No 12
R444
Figure 2. Nypa fruticans at provide — for construction and
Talalla (A) and young mixed fire wood, ethnomedicinal
mangrove fringes at
products, fishing habitat, coastal
Rekawa (B) show damage
protection and so on.
caused by the tsunami,
In late 2001, we interviewed
whereas interior mangrove
local inhabitants on the Indian
zones and land areas were
largely unaffected. Young subcontinent — the region
N. fruticans shoots are now second-hardest hit by last
regenerating (LPJ).
December’s tsunami — asking
about the extent to which
mangroves protected their
homesteads against disastrous
‘water-related’ events: cyclones
and wave action, but also
tsunamis and sea level increases.
They substantiated their view
well; one interviewee noted:
“during the recent devastation by
tropical cyclone 07B (November
6th, 1996) areas where
mangroves were in relatively
good condition were saved from
the fury of the cyclone and its
associated flooding events as
opposed to adjacent places
where mangroves had been
converted to shrimp farms”.
Similarly, in the Philippines, such
traditional ecological knowledge
In the aftermath of the Indian from socio-economic and of fisherfolk indicated that
Ocean tsunami, which killed over ethnobiological surveys that mangroves have a protective
a quarter million people and left focus on the services of buffering function [6,7].
millions homeless, experts and mangrove forests. Over the last In January 2005, we conducted
the media wondered how many several years, our teams have preliminary post-tsunami surveys
lives might have been saved if conducted interviews with local in 24 mangrove lagoons and
only we had not destroyed our people in Mexico, Gambia, estuaries in Sri Lanka’s coastal
mangrove forests. Others, Cameroon, Tanzania, Kenya, zones along the South-West,
however, were more skeptical, India, Sri Lanka and Vietnam, and South and South-East coasts of
countering: “fear of big waves is inquired about their relationships the island. The districts visited
no reason to plant mangroves” with mangrove forests, and about were heavily hit and counted at
[2]. What, then, is the role of the services that these forests least 23,558 deaths, more than
mangroves, and how many lives
might they have saved?
Box 1
Despite the popular and widely
accepted view that mangroves act Are all plants in the mangrove environment true mangrove species?
as living dykes [3], there is
surprisingly little data available to
test that hypothesis. The Mangrove plants are commonly subdivided into major components (true, strict or
important question is what future exclusive mangrove species), minor components (non-exclusive mangrove
role should mangrove forests play species) and mangrove associates. The major components feature a complete
fidelity to the mangrove environment, pure stands, morphological and
in coastal zone management and
physiological adaptations and taxonomic isolation [19]. An additional distinction
protection? The answer will not be
should be made between mangroves that are disturbance-resistant (for example
simple, as there are a lot of
Excoecaria agallocha), euryhaline (for example Avicennia marina) or fairly well
different types of mangrove forest
adapted to freshwater (for example Sonneratia caseolaris), on the one hand, and
in a wide variety of settings, and
those that are most ecologically vulnerable, most valuable and impacted from an
in some places mangroves are
ethnobotanical point of view, and those considered most characteristic of mature
simply absent from the natural
natural mangroves from an aesthetical point of view (for example
environment.
Rhizophoraceae), on the other hand [9,18]. This distinction is required to help
Apart from occasional
detect ‘cryptic ecological degradation’, in which introgressive mangrove-
observations and photographic
associated vegetation or minor mangrove species slowly start to dominate a
evidence of uprooted terrestrial
forest of true mangrove species (qualitative degradation) without loss of spatial
trees [4,5], the closest scientific
extent (no change or an increase in area) [9].
evidence for the buffering
function of mangroves comes
Magazine
R445
Figure 3. Two forest areas
80% of the total Sri Lankan death
near Talalla (A) and
toll [8]. Aided by previous field
Kahandamodara (B), which
knowledge, we assessed the
had become largely
following five characteristics dominated by mangrove
semi-quantitatively: (A) the pre- associates — cryptic
tsunami extent of the front ecological degradation —
have been destroyed by
mangrove (the first 500m fringe,
the tsunami. It is very
taking into account that this is a
unlikely that these areas
conservative width able to
have the potential to be
provide protection against a recolonized by original true
tsunami); (B) the extent of mangrove representatives,
mangroves already destroyed because less than a month
after the tsunami,
before the tsunami; (C) the
Acrostichum aureum was
‘naturalness’ of the mangrove, in
showing signs of strong
terms of the presence or absence
regeneration (C) (LPJ).
of cutting activities and of cryptic
ecological degradation [9]; (D)
tsunami damage to the front
mangrove; and (E) tsunami
damage to lives and properties in
the back mangrove and behind
the mangrove. These
characteristics were compiled
into the pre-tsunami mangrove
status (A+B), the presence of
cryptic ecological degradation
(C), and the destruction by the
tsunami (D+E), and a cluster
analysis (group average), using
PRIMER version 5.2.8, was
performed based on Bray-Curtis
similarity (Figure 1).
Our results show that, where
mangroves occur in the districts
visited, they did in fact offer
protection. Apart from some
isolated trees of Excoecaria
agallocha L., there were no
records of uprooted adult
mangrove trees. At most,
mangrove fringes near the water
edge took all the energy and were
damaged (Figure 2). Creek-
fringing Nypa fruticans (Mangrove splits indicate whether ‘cryptic A more in-depth ‘crime-scene
palm) had its leaves bent or torn ecological degradation’ occurred investigation’ is urgently needed,
off, but anchoring protection of (Figure 1). Mangrove sites with no but at present our conclusions
this plant by its rhizomatous stem cryptic ecological degradation, or are that three factors can
allowed new young leaves to those well protected by distance undermine the ability of
emerge less than a month after inland and by Rhizophora spp. mangroves to protect coastal
the tsunami impact. Other true fringes, all experienced a low villages: first, complete clearance;
mangrove representatives (Box 1) destructive impact from the second, insufficient regrowth
such as Sonneratia spp., the stem tsunami. The key feature of those following a previous clearing; and
of which can measure several forests that were damaged third, infusion of adult mangroves
meters in circumference, or appears to be a prominence of (where present) with excess of
Rhizophora spp. or Bruguiera vegetative associates not typical non-mangrove vegetation
spp., which has wide prop or knee of natural mangrove forests (Box components.
roots, also stood firm against the 1). The important lesson is that, It is important to recognize that
ocean surge. even though a coastal area might any compromising of mangrove
Forests dominated by less superficially seem to be ‘protective function’ is relevant to
typical mangrove associates protected by a mangrove forest, a wide variety of storm events,
(Box 1), however, were severely that habitat could be cryptically and not just tsunamis. Whereas
damaged (Figure 3A,B). This is degraded and not offer the the Indian Ocean area counted
also evident from the desired storm protection (see ‘only’ 63 tsunami events between
dendrogram, where the major also [9,10]). 1750 and 2004, there were more
Current Biology Vol 15 No 12
R446
Figure 4. Sand dune tremendous ecosystem services,
vegetation and Casuarina including protection against
equisetifolia plantations
extreme weather events and
may contribute to a
natural catastrophes [17]. When
reduced impact by ocean
we fail to raise awareness about
surges.
these functions, and we destroy
However, it should also be
or degrade the world’s natural
investigated to which extent
negative ecological influ- ecosystems too much, we do so
ences occur from such arti- at our own peril.
ficially planted barriers. (A)
Hambantota, (B) Tissamara-
Acknowledgments
hama, S. Sri Lanka coast
The first author is a Postdoctoral
(LPJ).
Researcher of the Fund for Scientific
Research (FWO-Vlaanderen). This
research is within the objectives of the
International Geosphere-Biosphere
Programme (IGBP), Past Global
Changes (PAGES) Focus 5: Past
Ecosystem Processes and Human-
Environment Interactions. We thank T.
Jayasingam (Eastern University, Sri
Lanka) for fieldwork logistics and Peter
Kareiva (The Nature Conservancy, USA)
for comments on our manuscript drafts.
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Batelaan, O., Sooriyarachchi, S.,
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in Sri Lanka affect biota and human entice bees to switch from a
Correspondences
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lagoons. Curr. Biol. 15, 579–586.
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A new mode of
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17 ‘observer’ and ‘demonstrator’
Koedam, N. (2002). Regeneration
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information bees from three Bombus
Creek, Kenya: a compromised or terrestris colonies in a flight
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Sussex).
Lars Chittka this article online), all providing
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Chan, J.C.-W., Jayatissa, L.P., and equally high amounts of 2 M
Koedam, N. (2005). Qualitative Pollinating insects have provided sucrose solution ad libitum.
distinction of congeneric and
one of the most enlightening At the start of a trial, a
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Bumblebees forage in highly introduced the seven alternative
the sustainable management of
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tropical coastal ecosystems.
Environ. Dev. Sustain. 4, 93–112. flower choices of conspecifics arena. The naïve observer bee
14. Chan, H.T. (1996). Mangrove
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reforestation in Peninsular
date information about current choose one inflorescence to
Malaysia: a case study of Matang.
reward levels. Nonetheless, forage upon.
In Restoration of Mangrove
interactions between foragers in In this first trial, when
Ecosystems, C.D. Field, eds.
(Okinawa: International Society for the field have been largely observers were entirely unfamiliar
Mangrove Ecosystems).
viewed in an antagonistic with both species, bees strongly
15. Kairo, J.G., Dahdouh-Guebas, F.,
context, where scent marks left preferred the occupied
Bosire, J., and Koedam, N. (2001).
by foragers on flowers act as a inflorescence (Figure 2A; binomial
Restoration and management of
deterrent to other bees [1]. Here test p < 0.01) over the seven
mangrove systems – A lesson for
and from the East African region. S. we show, conversely, that unoccupied options. As
Afr. J. Bot. 67, 383–389.
foraging conspecifics can not demonstrators had not chosen
16. WI–IP. (2005). Tsunami of Aceh and
only increase the attractiveness the inflorescence that they
North Sumatra. (Bogor, Wetlands
of an inflorescence, but also foraged upon themselves, or
International – Indonesia
Programme).
17. Stokstad, E. (2005). Taking the
pulse of Earth’s life-support
systems. Science 308, 41–43.
18. Jayatissa, L.P., Dahdouh-Guebas,
F., and Koedam, N. (2002). A review
of the floral composition and
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19. Tomlinson, P.B. (1986). The Botany
of Mangroves. (Cambridge:
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1Biocomplexity Research Team, c/o
2General Botany and Nature
Management, Mangrove Management
Nestbox
Group, Vrije Universiteit Brussel,
Pleinlaan 2, B-1050 Brussels, Belgium.
1E-mail: fdahdouh@vub.ac.be
3Department of Botany, University of Current Biology
Ruhuna, Matara, Sri Lanka. 4Kenya
Marine and Fisheries Research Institute,
Figure 1. Choice array.
PO Box 81651, Mombasa, Kenya.
5Institut Français de Pondichéry, Rue Eight equally and highly rewarding inflorescences, each containing three flowers, were
St. Louis 11, BP 33, 605 001 presented to the observer bee in a 105 x 70 x 30 cm flight arena connected to the
Pondicherry, India. nestbox.
R443
substrates depend on binding at
Essay
this site, there are probably
additional substrate recognition
sites. Another contribution to
How effective were mangroves as a
substrate selection is made by
scaffold proteins, e.g. AKAP79,
defence against the recent tsunami?
which target the phosphatase to
neuronal synapses or other
cellular sites. Calcineurin also Whether or not mangroves function as buffers against tsunamis is the
delegates work to protein subject of in-depth research, the importance of which has been
phosphatase 1 (PP1) through a neglected or underestimated before the recent killer tsunami struck. Our
phosphatase cascade, in which preliminary post-tsunami surveys of Sri Lankan mangrove sites with
dephosphorylation of the PP1 different degrees of degradation indicate that human activity
antagonists DARPP-32 or exacerbated the damage inflicted on the coastal zone by the tsunami.
inhibitor-1 by calcineurin relieves
their inhibitory effect on PP1, and
F. Dahdouh-Guebas1*,
allows PP1 to act on its own their large above-ground aerial
L.P. Jayatissa3*, D. Di Nitto1,
preferred substrates. root systems and standing crop.
J.O. Bosire4, D. Lo Seen5 and Like many habitats, mangrove
N. Koedam2
What are its inhibitors? forests have been degraded and
Cyclosporin A (CsA) and FK506 destroyed by humans, and their
bind tightly to the abundant Mangrove forests have iconic loss is a source of global concern.
In the second half of the 20th
intracellular proteins cyclophilin A status as natural ecosystems that
and FKBP12, respectively, and provide services to humans. They century, 50% of the world’s
the resulting ligand–protein function as breeding, spawning, mangrove forests have been
complex binds to calcineurin and hatching and nursing grounds for destroyed, and current annual
impedes access of protein marine and pelagic species, and loss rates vary from 1 to 20% [1].
substrates to the active site. are important in the daily Ironically, the great human
Blockade of a biological process livelihood of local human tragedy of the recent December
26th tsunami may provide the
by CsA and independently by subsistence communities.
FK506 is diagnostic for Mangrove representatives such as stimulus for a better
calcineurin involvement. Other Rhizophora spp. also function as a understanding of what mangrove
inhibitors that find frequent physical barrier against tidal and forests can and cannot do for
experimental use are the ocean influences by means of human well-being.
autoinhibitory peptide from
calcineurin and fragments of the 6. Walawey Ganga E.
8. Kahandamodara L.
regulatory proteins Relatively good pre-tsunami 9. Rekawa L.
mangrove status 11. Dickwella
DSCR1/MCIP/calcipressin/Rcn1p, 12. Talalla L.
Cryptic
Cabin1/cain, and AKAP79. 20. Akurala
ecological
18. Galle-Unawatuna
degradation
17. Koggala L.
Does it have any medical 21. Balapitiya E.
1. Batticaloa L.
relevance? Calcineurin signalling 7. Kalametiya L.
is prominent in transplant 13. Devinuwara L.
Bad pre-tsunami 14. Nilwala Ganga E.
rejection and autoimmune mangrove status 15. Polwatumodara
16. Kapparatota
disease, where the inhibitors CsA
19. Ginganga E.
and FK506 are used clinically, and 4. Palatupana L.
5. Kirinda L.
is being studied for its No 9. Kirama Oya mouth
contribution to myocardial cryptic 22. Kosgoda
ecological 23. Bentota Ganga E.
hypertrophy and to virulence in degradation
24. Kaluwamodara
fungal pathogens. 2. Komari L.
Relatively good pre-tsunami
3. Pottuvil L.
mangrove status
100
90
80
70
60
Where can I find out more? Similarity Current Biology
Aramburu, J., Rao, A., and Klee, C.B.
(2000). Calcineurin: from structure
Figure 1. Dendrogram generated by a cluster analysis of the 24 mangrove sites
to function. Curr. Top. Cell. Regul.
investigated, indicating their characteristics and the impact of the tsunami (big wave,
36, 237–295.
severely impacted; small wave, little impacted).
Rusnak, F., and Mertz, P. (2000).
Calcineurin: form and function. The ‘mangrove status’ is a combination of pre-tsunami aerial extent of the front man-
Physiol. Rev. 80, 1483–1521. grove and pre-tsunami mangrove destruction (see text). The tsunami had only a small
impact on lagoons that show no cryptic ecological degradation (sites 2, 3, 23 and 24)
or that are protected by the distance from the shore and by frontal Rhizophora spp.
fringes (sites 17, 18 and 21). The lagoons are numbered clockwise from East to West,
The CBR Institute for Biomedical
to emphasize that damage was not linked to geographic position in view of tsunami
Research and Department of Pathology,
wave energy. A map overview of all lagoons can be found in Jayatissa et al. [18], with
Harvard Medical School, Boston,
the exception of Batticaloa, Komari and Potuvil, which are located at the easternmost
Massachusetts 02115, USA.
extremity of the island. L, Lagoon; E, Estuary.
E-mail: hogan@cbr.med.harvard.edu
Current Biology Vol 15 No 12
R444
Figure 2. Nypa fruticans at provide — for construction and
Talalla (A) and young mixed fire wood, ethnomedicinal
mangrove fringes at
products, fishing habitat, coastal
Rekawa (B) show damage
protection and so on.
caused by the tsunami,
In late 2001, we interviewed
whereas interior mangrove
local inhabitants on the Indian
zones and land areas were
largely unaffected. Young subcontinent — the region
N. fruticans shoots are now second-hardest hit by last
regenerating (LPJ).
December’s tsunami — asking
about the extent to which
mangroves protected their
homesteads against disastrous
‘water-related’ events: cyclones
and wave action, but also
tsunamis and sea level increases.
They substantiated their view
well; one interviewee noted:
“during the recent devastation by
tropical cyclone 07B (November
6th, 1996) areas where
mangroves were in relatively
good condition were saved from
the fury of the cyclone and its
associated flooding events as
opposed to adjacent places
where mangroves had been
converted to shrimp farms”.
Similarly, in the Philippines, such
traditional ecological knowledge
In the aftermath of the Indian from socio-economic and of fisherfolk indicated that
Ocean tsunami, which killed over ethnobiological surveys that mangroves have a protective
a quarter million people and left focus on the services of buffering function [6,7].
millions homeless, experts and mangrove forests. Over the last In January 2005, we conducted
the media wondered how many several years, our teams have preliminary post-tsunami surveys
lives might have been saved if conducted interviews with local in 24 mangrove lagoons and
only we had not destroyed our people in Mexico, Gambia, estuaries in Sri Lanka’s coastal
mangrove forests. Others, Cameroon, Tanzania, Kenya, zones along the South-West,
however, were more skeptical, India, Sri Lanka and Vietnam, and South and South-East coasts of
countering: “fear of big waves is inquired about their relationships the island. The districts visited
no reason to plant mangroves” with mangrove forests, and about were heavily hit and counted at
[2]. What, then, is the role of the services that these forests least 23,558 deaths, more than
mangroves, and how many lives
might they have saved?
Box 1
Despite the popular and widely
accepted view that mangroves act Are all plants in the mangrove environment true mangrove species?
as living dykes [3], there is
surprisingly little data available to
test that hypothesis. The Mangrove plants are commonly subdivided into major components (true, strict or
important question is what future exclusive mangrove species), minor components (non-exclusive mangrove
role should mangrove forests play species) and mangrove associates. The major components feature a complete
fidelity to the mangrove environment, pure stands, morphological and
in coastal zone management and
physiological adaptations and taxonomic isolation [19]. An additional distinction
protection? The answer will not be
should be made between mangroves that are disturbance-resistant (for example
simple, as there are a lot of
Excoecaria agallocha), euryhaline (for example Avicennia marina) or fairly well
different types of mangrove forest
adapted to freshwater (for example Sonneratia caseolaris), on the one hand, and
in a wide variety of settings, and
those that are most ecologically vulnerable, most valuable and impacted from an
in some places mangroves are
ethnobotanical point of view, and those considered most characteristic of mature
simply absent from the natural
natural mangroves from an aesthetical point of view (for example
environment.
Rhizophoraceae), on the other hand [9,18]. This distinction is required to help
Apart from occasional
detect ‘cryptic ecological degradation’, in which introgressive mangrove-
observations and photographic
associated vegetation or minor mangrove species slowly start to dominate a
evidence of uprooted terrestrial
forest of true mangrove species (qualitative degradation) without loss of spatial
trees [4,5], the closest scientific
extent (no change or an increase in area) [9].
evidence for the buffering
function of mangroves comes
Magazine
R445
Figure 3. Two forest areas
80% of the total Sri Lankan death
near Talalla (A) and
toll [8]. Aided by previous field
Kahandamodara (B), which
knowledge, we assessed the
had become largely
following five characteristics dominated by mangrove
semi-quantitatively: (A) the pre- associates — cryptic
tsunami extent of the front ecological degradation —
have been destroyed by
mangrove (the first 500m fringe,
the tsunami. It is very
taking into account that this is a
unlikely that these areas
conservative width able to
have the potential to be
provide protection against a recolonized by original true
tsunami); (B) the extent of mangrove representatives,
mangroves already destroyed because less than a month
after the tsunami,
before the tsunami; (C) the
Acrostichum aureum was
‘naturalness’ of the mangrove, in
showing signs of strong
terms of the presence or absence
regeneration (C) (LPJ).
of cutting activities and of cryptic
ecological degradation [9]; (D)
tsunami damage to the front
mangrove; and (E) tsunami
damage to lives and properties in
the back mangrove and behind
the mangrove. These
characteristics were compiled
into the pre-tsunami mangrove
status (A+B), the presence of
cryptic ecological degradation
(C), and the destruction by the
tsunami (D+E), and a cluster
analysis (group average), using
PRIMER version 5.2.8, was
performed based on Bray-Curtis
similarity (Figure 1).
Our results show that, where
mangroves occur in the districts
visited, they did in fact offer
protection. Apart from some
isolated trees of Excoecaria
agallocha L., there were no
records of uprooted adult
mangrove trees. At most,
mangrove fringes near the water
edge took all the energy and were
damaged (Figure 2). Creek-
fringing Nypa fruticans (Mangrove splits indicate whether ‘cryptic A more in-depth ‘crime-scene
palm) had its leaves bent or torn ecological degradation’ occurred investigation’ is urgently needed,
off, but anchoring protection of (Figure 1). Mangrove sites with no but at present our conclusions
this plant by its rhizomatous stem cryptic ecological degradation, or are that three factors can
allowed new young leaves to those well protected by distance undermine the ability of
emerge less than a month after inland and by Rhizophora spp. mangroves to protect coastal
the tsunami impact. Other true fringes, all experienced a low villages: first, complete clearance;
mangrove representatives (Box 1) destructive impact from the second, insufficient regrowth
such as Sonneratia spp., the stem tsunami. The key feature of those following a previous clearing; and
of which can measure several forests that were damaged third, infusion of adult mangroves
meters in circumference, or appears to be a prominence of (where present) with excess of
Rhizophora spp. or Bruguiera vegetative associates not typical non-mangrove vegetation
spp., which has wide prop or knee of natural mangrove forests (Box components.
roots, also stood firm against the 1). The important lesson is that, It is important to recognize that
ocean surge. even though a coastal area might any compromising of mangrove
Forests dominated by less superficially seem to be ‘protective function’ is relevant to
typical mangrove associates protected by a mangrove forest, a wide variety of storm events,
(Box 1), however, were severely that habitat could be cryptically and not just tsunamis. Whereas
damaged (Figure 3A,B). This is degraded and not offer the the Indian Ocean area counted
also evident from the desired storm protection (see ‘only’ 63 tsunami events between
dendrogram, where the major also [9,10]). 1750 and 2004, there were more
Current Biology Vol 15 No 12
R446
Figure 4. Sand dune tremendous ecosystem services,
vegetation and Casuarina including protection against
equisetifolia plantations
extreme weather events and
may contribute to a
natural catastrophes [17]. When
reduced impact by ocean
we fail to raise awareness about
surges.
these functions, and we destroy
However, it should also be
or degrade the world’s natural
investigated to which extent
negative ecological influ- ecosystems too much, we do so
ences occur from such arti- at our own peril.
ficially planted barriers. (A)
Hambantota, (B) Tissamara-
Acknowledgments
hama, S. Sri Lanka coast
The first author is a Postdoctoral
(LPJ).
Researcher of the Fund for Scientific
Research (FWO-Vlaanderen). This
research is within the objectives of the
International Geosphere-Biosphere
Programme (IGBP), Past Global
Changes (PAGES) Focus 5: Past
Ecosystem Processes and Human-
Environment Interactions. We thank T.
Jayasingam (Eastern University, Sri
Lanka) for fieldwork logistics and Peter
Kareiva (The Nature Conservancy, USA)
for comments on our manuscript drafts.
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1Biocomplexity Research Team, c/o
2General Botany and Nature
Management, Mangrove Management
Nestbox
Group, Vrije Universiteit Brussel,
Pleinlaan 2, B-1050 Brussels, Belgium.
1E-mail: fdahdouh@vub.ac.be
3Department of Botany, University of Current Biology
Ruhuna, Matara, Sri Lanka. 4Kenya
Marine and Fisheries Research Institute,
Figure 1. Choice array.
PO Box 81651, Mombasa, Kenya.
5Institut Français de Pondichéry, Rue Eight equally and highly rewarding inflorescences, each containing three flowers, were
St. Louis 11, BP 33, 605 001 presented to the observer bee in a 105 x 70 x 30 cm flight arena connected to the
Pondicherry, India. nestbox.