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Samoa Tsunami Rapid Environmental Impact Assessment (EIA) Recommendations
(October 3
rd
to 7
th
2009)
Contributors: Government of Samoa, Ministry of Natural Resources and Environment; Pacific Islands Programme Conservation International;
Secretariat for the Pacific Regional Environment Programme; UNESCO; UNDP; UNEP
Cluster: Early Recovery (Head Georgina Bonin, UNDP Apia, Samoa)
Context
The environment sub-cluster was tasked by the Prime Minister to carry out a rapid environmental impact and needs assessment to be
included in the assessment for the Rapid Recovery Cluster. Nearly all coastlines that were affected by the tsunami were visited and
systematically assessed with an expert team between October 3
rd
to 7
th
2009 – hence starting four days after the Tsunami itself.
Assessments for remaining small sections of coastline without road access had to rely on aerial photographs. Agriculture (including
horticulture) is being assessed by the Ministry of Agriculture and Fisheries in collaboration with FAO and reported on separately. A detailed
account of the EIA is appended to the Summary Framework and available from the Apia office of UNEP (contact Dr Greg Sherley care of
UNDP).
General Observations
•
Significant environmental damage was sustained on the south and east coast of Upolu and Manono island including coastal erosion,
salinisation of coastal areas, damage from building debris and pollution from solid waste and sewage in village areas
•
Sensitive marine habitats including coral reefs and seagrass beds are expected to have sustained significant damage
•
Environmental damage was greatest at the far eastern and southern coast of Aleipata and generally diminished westwards
•
Bathymetry and coastal morphology and topography, including distance of reef from shore and the location of channels had a major
influence on the damage sustained
•
More detailed environmental assessments are needed especially for sensitive marine habitats such as coral reefs and seagrass beds
and terrestrial ecosystems such as coastal marshes, mangrove areas and near shore islands.
Initial Marine Assessment
Impact/Vulnerability Recommendation
Submerged marine habitat (coral reefs,
lagoons, sea-grass) -expected high impact
(physical damage) in Aleipata and Falealili
districts. Impact becomes patchy but still
significant further west (e.g.Tafitoala).
Plan and resource a comprehensive and safe in-water marine assessment. Include focus on
damaged areas where previous information exists e.g. Aleipata and Safata MPAs and fish reserves.

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Physical damage to the corals will
predispose them to disease (bacterial,
fungal) and further loss of reef biodiversity.
Ava/channels - clear that ava (channels)
funneled the wave inland causing greater
damage in these areas
Beaches and foreshore – heavily
impacted, significant removal of sand and
adjacent land based sediment.
Natural recovery should be monitored and additional stressors be minimized (e.g. reclamation sand
mining, commercial fishing harvest).
Channel impact patterns need to be considered in terms of rebuilding settlements because they
indicate permanent higher hazard zones.
Requires stabilization in the short term to prevent further sand/sediment loss especially in advance
of rainy season and restoration in the longer term. New impacts e.g. reclamations, and mining
should not be allowed in impacted areas. Multi-disciplinary approach to restoration required.
Increased use or repair of seawalls needs to be carefully considered because their use can be
negative e.g. by giving the wave “teeth”
Debris and solid waste in lagoon and
reef -significant debris from land in lagoon,
possible debris on outer reefs. Some
debris will pose health risk.
Manual clean-up (not dredging) of lagoon areas is necessary. Reusable and recyclable material will
need to be sorted.
Debris/rubbish in mangroves and on
beaches -significant debris eg housing
material
Clean-up & remove debris after useful material has been salvaged by owners and villagers.
Sedimentation -high expected impact of
sediment including scouring by sand and
expected smothering of coral from
sediments (sand and earth). Likely cause
major changes in habitat/species
composition and reduced ability to support
food resources.
Sedimentation impact must be considered in marine assessment of reef and fisheries impact.
Beaches/foreshore/land based sources e.g. streams need to be stabilized to reduce ongoing impact
especially with advent of rainy season.
Pollution - Potential contamination from
sewage, hydrocarbons, possible
agricultural chemicals, organic waste,
pesticides
In heavily impacted areas, communities should be warned against harvesting lagoon food resources
(particularly shellfish) until assessments have proved them safe to eat.
Marine Protected Areas and Fisheries
Reserves -high impact.
Must be considered in marine assessment: many reserve areas compromised in terms of ongoing
ability to support regeneration of marine food sources outside of these zones.

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Early remarking of fish reserves and MPA no-take zones and assessment of these areas to be able
to recover and still be functional (some may need to be relocated).
Pre-impact information from these sites is available and valuable to assess true impact (short and
longer term) – should be a key focus of marine assessment.
Marine Food Sources compromised in
impacted areas – The combined affect of
the aforementioned impacts may influence
marine food resources with respect to
volume, quality and safety.
Communities will need to have the ability to replace or substitute traditional marine subsistence food
sources with other food sources e.g. access to fish from outside of the district.
Safety of marine food sources needs to be assessed (e.g. shellfish from contamination) in impacted
and vulnerable areas.
Boat capacity should focus initially on helping impacted villages get access to offshore fish
resources e.g. replacement of Alias. Consider a possible ban on commercial access to offshore
resources in these areas.
Restore inshore boat capacity (e.g. Alia’s and pao pao need extensive rebuilding).
Aleipata Wharf - Serious damage has
been incurred on the wharf and there has
been significant impact on the only large
seagrass bed in the district.
Pollution has probably occurred (e.g. oils
and fuel).
There is high concern about the continued
vulnerability of the area with regard to the
wharf rebuild
Recovery of oil drums that were washed away (approximately 40 x 44 gallon drums are
unaccounted for) and any other loss of chemicals/fuels assessed. Area must be safety certified.
Significant debris clean up and stabilization of wharf are required. There is a high risk of increased
sedimentation of the surrounding marine environment with advent of the rainy season washing
unstabilised sediments into the sea.
Local people should be warned against harvesting lagoon food resources from the wharf area until
samples have been taken, assessments done and safety certification notified.
An in depth environmental risk assessment is required before a decision to rebuild is taken.

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Initial Terrestrial Assessment
Impact Recommendations
Solid Waste - Large volumes of solid
waste (including vehicles). Some waste
aggregation has begun but clearing and
disposal is still a significant issue
Solid waste management plan including sorting waste into disposable, hazardous and recyclable.
Note the Japanese International Cooperation Agency has started a clean up project.
Illegal/improper dumps exposed by wave
action with consequent solid waste
pollution issues (e.g. Tuialemu, Lalomanu)
Cleanup of dumps and proper disposal of waste – has implications for human health, hygiene,
vermin etc
Review and write a new plan for local waste collection process.
There are implications around this issue regarding revival of tourism in these areas.
Coastal Impacts - Patterns of high wave
impact clearly observed with implications
for future land use.
Implement CIMP (Coastal Infrastructure Management Plans) for coastal areas
Ensure that findings from incoming geo-science teams are fed into planning processes including
revision of CIMP plans as required
Observed damage to sensitive coastal
ecosystems eg. Marshlands and river
habitats. This may have impacted some
fish nurseries and some of these sites
include unique ecosystems.
Clean-up of trash and debris required.
All sensitive areas need to be assessed. Identify potential restoration activities
Salinisation of coastal lowland areas.
Some coastal trees are stressed and
losing leaves but observations showed that
others are resilient.
Replanting in these areas should focus on native salt tolerant species and species that are able to
hold the coastline together. In addition, ability to withstand wave damage is important for replanting
near settlements as shallow rooting trees can be uprooted.
Evidence of seawall rocks displaced by the
Tsunami causing significant damage up to
50 metres inland
Rebuild to proper standards according to codes of environmental practice as appropriate – in some
areas natural alternatives may be preferable
Waterways - Riverine systems were
heavily impacted along the coasts up to I
km inland, due to funneling affect of valley
systems
Formal and detailed assessment of impacts.
Plan activities to mitigate potential future impacts
Sewerage - Septic tanks were displaced/
emptied/ uncovered with obvious negative
environmental and human health impacts
Pump clean at risk tanks.
Replace with septic tanks that meet appropriate health and environmental standards as per
resettlement protocols
Agriculture and horticulture - Noted
impacts on agricultural crops eg. Taro,
bananas, breadfruit etc
MAF and FAO have surveyed this and will provide recommendations

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Results of the Environmental Impact Assessment with implications and relevant information for Disaster Risk Reduction will be
included in the final report.
Many of the impacts of the tsunami may have been mitigated if the CIMPs had been fully implemented. Preparation of a tsunami hazard zone
map for the Samoa archipelago is required. In addition a review of the national coastal hazard zone mapping assessment is required together
with a review of the content of the CIMPs and implementation requirements.
Available capacity to meet identified needs (notes - this list is not comprehensive; potential partners highlighted)
Marine related – University of the South Pacific (USP) and South Pacific Geoscience Commission (SOPAC) scientists are ready and willing
to travel to Samoa. CI has funds ear-marked to support further EIA work and are prepared to assist a Samoan Government led. SPREP has
marine pollution expertise which could be available upon request.
Solid waste (on land) – Japanese International Cooperation Agency (JICA) has started assessing the quantity of the solid waste and have
plans to fund a clean up programme. SPREP has solid waste expertise which could be available upon request.
Coastal Infrastructure Management Plan - Samoan Government agencies have capacity, as do local consultants, such as the Pacific
Environmental Consultants (PECL).
Marine protected area management – Conservation International (CI), SPREP.