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    Technical Report
    Environmental impact assessment for the reconstruction of Guraidhoo Harbour, Thaa Atoll, Maldives
    (2015-12) Maldives Energy and Environmental Company
    The Ministry of Housing and Infrastructure requested the services of Maldives Energy and Environmental Company (MEECO) to provide an Environmental Impact Study (EIA) for the re-construction of harbour at Guraidhoo Island, Thaa Atoll. The assessment addresses specific key issues stated in the Terms of Reference (TOR) as agreed between EPA and the Proponent following the Scoping Meeting held on the matter. This EIA report was prepared for the fulfilment of the requirements of the Environmental Impact Assessment Regulations, 2012 with the purpose of conducting an assessment of possible impacts on biophysical and human environment arising from proposed development project. The project is proposed by Ministry of Housing and Infrastructure, Maldives. The proposed harbour reconstruction project include the following components; 1. Reconstruction of improved breakwaters for harbour basin and entrance channel; 2. Reconstruction of improved main quay wall and a side quay wall; 3. Maintenance dredging of the harbour; 4. Extension of the harbour basin; 5. Reclamation of small area of land by dredge sediment disposal; 6. Construction of revetments on a 14m section for the newly reclaimed land; 7. Installation of navigational lights. The present harbour facility at the Guraidhoo Island is greatly damaged and is not serving its intended function of providing safe access to the island and safe mooring of vessels. Additionally, the size of the harbour is identified as inadequate for the present need and expected economic growth of the island. The harbour forms a key part in many livelihood activities of the island and is frequently used by passenger and cargo vessels as well as vessels travelling to and from Laamu atoll. Hence, the improvement of harbour facility will greatly benefit the island community while also enabling future economic development at the island. The proposed project is not expected to cause any long term major irreversible environmental impacts, though few temporary impacts during the construction phase is expected. These impacts can be successfully mitigated by following the measures recommended in this EIA. The construction phase of the project is also expected to present several negative socio-cultural and economic impacts, which can also be mitigated by following measures presented in this EIA. Overall, the project is expected to yield major positive impacts in socio-cultural and economic sector when the new harbour comes into operation. Based on the results of the assessments, this EIA study concludes that with the proposed mitigation in place, the project is justifiable, would be environmentally acceptable and could proceed in compliance with the relevant environmental legislations and regulations. In this EIA, the consultants have proposed an Environmental management plan to ensure that the construction phase of the project does not cause major unexpected impacts on the environment as well as to ensure that the proposed measures are working effectively to safeguard the environment.
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    Technical Report
    Environmental impact assessment for rehabilitation and repair of harbour at Inguraidhoo Island, Raa Atoll
    (2015-08) Maldives Energy and Environmental Company
    1. The Ministry of Housing and Infrastructure requested the services of Maldives Energy and Environmental Company (MEECO) to provide an Environmental Impact Study (EIA) for the rehabilitation and repair of the harbour, Inguraidhoo Island, Raa Atoll, Maldives. 2. The assessment addresses specific key issues stated in the Terms of Reference (ToR) as agreed between EPA and the Proponent following the Scoping Meeting held on the matter. 3. Inguraidhoo harbour was developed in 1998 by dredging into the island from the original coastline of the Island to create the required space for the harbour basin. Since then there was a major repair done in the year 2005, however, the repair and maintenance activity for the harbour had been performed was not adequate. Moreover, the island envision of expanding the basin to cater to the growing demand of increasing vessels in the island. 4. Inguraidhoo has a registered population of 1,842 people. Due to the poor design and workmanship during the construction of its existing harbour, it has failed to provide much anticipated protection and safety for the travellers and vessels. Consequently, the people of the island have suffered enormously. The present entrance channel creates dangerous situations particularly during the rough weather conditions. There had been several incidents of damages to the vessels, people and to property while trying to pass through the channel. In addition to the problems caused due to the deterioration of the breakwater, the original height of the seawall is not adequate to prevent overtopping of waves into the harbour basin creating very rough conditions during bad weather. Similarly the low height of the quay wall allows overtopping of waves into the coast causing flooding. 5. In order to alleviate the above problems the Proponent intends to rehabilitate the breakwater, extending the breakwater to provide protection for the harbour entrance, constructing revetment on the northern and southern ends of the harbour adjoining the land, maintenance dredging of shallow areas within the harbour basin and the entrance channel. 6. The Consultants assessed the potential environmental impacts using sound scientific methodology, literature review and experiences from the past projects of similar nature. In addition views and opinions of the key stakeholders have been reflected in the report. The main findings have been summarised in the following sub-paragraphs. a. Due to the critical role the harbour plays in the socio-economic development of the island, the existing problems associated with the harbour need to be addressed as a matter of priority. b. Environmental impacts assessment carried out for the project indicates that the project can be successfully implemented without an irreversible significant damages to the environment and that the socio-economic benefits to the community and the region far outweighs minor damages that may arise out of the project. c. The project, however, has inevitable low magnitude negative impacts, including, sedimentation over parts of the reef, noise and vibration due to piling and construction activities, pollution from solid and hazardous waste. Hence, the project shall put in place the mitigation measures prescribed in the report while undertaking the project activities. 7. The Inguraidhoo harbour maintenance and rehabilitation project is of utmost importance to the people of the island. The project is in line with the government’s policies and can be implemented in fully compliance with the relevant laws and regulations. The Proponent has given full commitment to undertake mitigation measures given in the report during the project implementation. Hence the negative impacts can be effectively mitigated through the prescribed actions and the project could be implemented successfully.
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    Technical Report
    First addendum to the environment impact assessment for Koodoo Domestic Airport extension and development of Airport Hotel at Koodoo Island, G. A. Atoll
    (2014-12) Maldives Energy and Environmental Company
    This is the first addendwn to the EIA report for Kooddoo Domestic airport extension and development of an Airport Hotel at Ga Kooddoo, GA Atoll. This addendum is prepared to address the changes brought to the concept plan of the Airport Hotel and the alternative sand borrow sites recommended in the EIA report. Major changes to the airport hotel concept include the change in nwnber of water villas from 25 to 43, re arrangement of water villas from semi-circular shape to arc-shape with double rows of water villas on the southern ann of the arc. With this change the total number of the rooms in Kooddoo Airport Hotel will increase to 68 rooms. In addition to this the size of the VIP lounge is increased and owner's villa is added at the southern end of the Hotel. With the above changes the total built up area of Kooddoo airport hotel will be increased from 13.41% to 15.43%. The alternative sand borrow site recommended in the EIA report, which was located as on the eastern lagoon of the island, was changed to two sites on southern and northern end of Kooddoo Island, adjacent to the proposed reclamation area respectively. The main reason for changing the alternative borrow area is because of the shallow lagoon depth and swell conditions on the eastern side of the island, which would require cutting an entrance channel for operation of the dredger. Cutting an entrance channel on the eastern side would have irreversible impact to the reef and island and logistical difficulties for the proponent. Baseline data collected during the initial survey nere seen to be sufficient for the purpose of the addendum, thus no additional data was collected for this report. Impact assessment due to the changes were also observed to be more or less similar, but the impact footprint of the development will be changed to include the dredging area on the northern end of the island. However, with proper implementation of the mitigation measures, anticipated impact of dredging could be limited and contained in the work area without widespread dispersion of suspended sediment plume. Therefore the proposed changes will not alter the over-all aspect of the project.
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    Technical Report
    Environmental impact assessment for development of drainage works and storm water infiltration galleries in H. DH. Kulhudhuffushi, Maldives
    (2014-09) Maldives Energy and Environmental Company
    Kulhudhuffitshi Island with a population of over 8900 people is the most populated island in the northern region of the country and is considered to be the third largest population in the Maldives. The island is currently the hub of all commercial activities in the north. Physical and infrastructure developments have although brought socio-economic improvements to the resident community it has also come at an environmental cost. Among the environmental issues faced to the island, stormwater flooding has been considered having impacts on the people in many different ways. Land reclamation, reclamation of the wetland, destruction of the coastal vegetation belt and increased use of vehicles on sandy roads without an engineered drainage system have all contributed to the occurrences of stormwater flooding in the island. In an attempt to address the issue of stormwater in Kulhudhuffushi, the Integrating Climate Change Risks into Resilient Island Planning Project (ICCRRIP) commissioned Male Water Supply and Sewerage Company (MWSC) and Engineering Consultant PVT. Ltd to undertake a study to identify technical options available to solve the flooding problem. Subsequently a report on the findings was submitted to ICCRRIP in 2013. The study proposed a number of options for stormwater management in the island. The recommended method being that stormwater from the gutters and soak pits be connected to a pipeline terminating into underground storage tanks consisting of blocks of AquaCell which has an extensive range of modular cell products and are known to provide an efficient and sustainable method of storing large volumes of run-off for water attenuation or soakaway applications. These underground water tanks would hold the water and release into the ground slow enough for the ground to be able to absorb water and ultimately re-charging the groundwater lens. The report divides the island catchment areas into four zones and recommends two flood prone areas in the northern and the southern part of the island for piloting flood control by this method. However, due to the limited financing available for the piloting flood control by this method. However, due to the limited financing available for the project, it has been decided to pilot the drainage activities in the north eastern region of the island only. This would involve diversion of storm water from six roads namely, Marukazu Magu, Miskiy Magu, Soafiya Higun, Madharusaa Magu, Dhanbu Magu and Orchid Magu. Approved project cost is MVR 16 million. Maldives Road Development Corporation (MRDC) has been selected as the contractor for the project while MWSC will supervise their work. MRDC intends to merge pilot project activities with the on-going road construction works. The project planning, design and surveying began in July 2014 and is entire project is expected to completed and handed over by the contractor during the first half of November. The site clearance and the earthworks is expected to start as soon as EIA clearance is sought and have been planned to be completed within about 30 days. hi order to proceed with the proposed drainage works and installation of the stormwater infiltration galleries and EIA was commissioned to obtain environmental clearance and the EIA was conducted based on the Terms of Reference agreed between the Consultant and the EPA. The EIA recognizes the importance and urgency of addressing the heavy rain associated flooding in Kulhudhuffushi based on the field investigations backed by Detailed Island Risk Assessment in Maldives (2007) and Detailed Island Risk and Vulnerability Assessment (2013). The impact analysis show no significant negative impact expected to be arising out of any activity associated with the project. Project involves minor excavations, potential dewatering, filling back and operation of vehicles and temporary enclosure of the project sites. These may have minor and temporary negative impacts to the scenic view and vista. Potential post-project negative enviromnental impact could arise out of breeding of mosquitos and pests in the tanks, in the pipeline and soakpits due to standing water. Through proper maintenance of the system the problem could be largely avoided. Potential socio-cultural impacts associated with the pilot project include, disruption to services, and temporary obstacles to right of way. Minor negative socio-cultural and environmental impacts associated with the project are temporary and reversible in nature. These further could be mitigated through appropriate mitigation measures. The most expected positive impact expected from the project will be improvement to the drainage. With the project the project is expected to alleviate drainage issue from an area measuring 175,000m2 of urban land with better drainage, and as indirect positive impacts, the project is expected to further improve groundwater, reduce potential contaminants reaching the marine environment, leading to improved public health and quality of life through reduced risk of waterborne and water-related diseases and increased public satisfaction with the urban environment. The project is expected to bring some minor positive impacts to the local economy during the three phases of the project as a results of temporary opportunities created during the works. Several major realistic and practical alternatives have been assessed including the 'no project alternative'. Without the project, the funds allocated for the project could be saved but may run the risk of losing it since the project may not have adequate time left before closure. Since, detailed designs, engineering drawings and contractor for the project has already been selected it would be completely unrealistic and wasteful to even consider utilizing the funds for a different activity. Considering meeting the objectives of the project, environmental and economical superiority of the alternatives evaluated, undertaking a pilot project in one of the flood prone area using underground tanks in empty available space for drainage has been found to the best practical option. The Council expressed their wish implement the project in the Zone A (the south east region) as opposed to Zone B (north east region). They were of the view that Zone A floods more severely compared to Zone B and therefore, the project would have greater impact by this shift. Considering that the detailed design has already been done for this zone, it is recommended to change the project location as suggested by the Council in order to increase public acceptability of the project. The intended positive impacts of the project can only be accurately determined by the post-project monitoring scheme. In order to ensure effectiveness of underground stomi water collection tanks in mitigating against flooding it is essential to monitor, collect information, evaluate the information collected and disseminated. With the following recommendations duly considered or addressed appropriately, the ETA found that the positive aspects of the project far outweigh its negative impacts. ■ Bank of Maldives Branch at Kulhudhuffushi have not been consulted during the design phase on the possible installation of an underground tank within their compound. ETA suggests that prior to the onset of ground work that the Bank be consulted for their consent. ■ Location identified for the tank at the football ground need to be relocated from the southwest corner to the northwest corner in order to reduce the pipeline length as well as the associated costs. ■ Capacity of the underwater tank proposed for Bank of Maldives' compound seem to be of inadequate capacity since it the region covers 53% of the total pilot project area. ■ It is not clear how the existing design will address the over-flow should such a situation arise. This issue need to be resolved prior to the construction. ■ Post project maintenance and management shall be discussed and agreed with the island council in order to avoid potential mosquito and other pest issues as a result of the project. If the pilot project is successful in managing storm water in the piloted area, the system will be expended to other regions of Kulhudhuffushi Island and similar systems it could be replicated elsewhere in the Maldives.
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    Technical Report
    Environmental impact assessment for resort development in K. Kuda Bandos, North Malé Atoll
    (2014-06) Riyaz, Mahmood; Zuhair, Mohamed; Shakir, Ibrahim
    In mid-2005 and early 2000 the government leased large number of uninhabited islands for development of picnic islands for a relatively low rent. Those picnic island were developed and most of them are used as exclusive high end tourist resort, but the revenue generated for the government from those islands are very low due to low land rent. Therefore in order to generate more revenue to the Government the cabinet during the MDP Government decided to eliminate all picnic island and allocated them for resort developments. This decision was enforced in 2012. In this respect if the picnic island is within 700m radius of an existing resort the government offered the island to the resort if they are willing to pay the acquisition cost of the island, which is about 6 million US$ per hectares. Malahini Holdings Pvt. Ltd, paid the acquisition cost of Kuda Bandos Island and decided to convert the island to a mixed local and foreign tourist resort retaining the local picnic concept, and established Malahini Holdings Pvt. Ltd which is a joint venture company with 10% share of the Government of Maldives. This is the Environmental Impact Assessment (EIA) report carried out for Malahini Holdings Pvt. Ltd to develop and operate a resort for mixed local and foreign tourist in K. Kuda Bandos Island located in North Central part of Malé Atoll. Kuda Bandos development project involves development and operation of 90 rooms, two and half-three star resort, with all the necessary facilities and amnesties. The EIA was prepared as fulfilment of the requirement by the Ministry Tourism (MoT) for granting permission for the project. Environmental Impact Assessment (EIA) of development projects is a requirement by the Environmental Protection and Preservation Act (EPPA) (law 4/93) of the Government of the Republic of Maldives. The total cost of the proposed project is approximately 13.5 million USD. The project will be developed within 18 months. The project will create a relatively large number of direct and indirect employment opportunities for the Maldives. Therefore the project will significantly contribute to the economic growth, particularly tourism sector, and other relevant socioeconomic activities. This report has been prepared in accordance with the Environmental Impact Assessment Regulations published by the Ministry of Environment and Energy 2012 and covers both negative and positive environmental and socio-economic impact arising from the proposed project in Kuda Bandos Island. Major findings of this report are based on information gathered during the field inspection of both the existing environment and possible effects of the project activities, through extensive literature review and experiences gained from similar projects elsewhere in the Maldives. The proposed project activity will take place on Kuda Bandos Island, an uninhabited island lies in an N-S oriented triangular shape reef on the central part of North Malé Atoll. The island is situated on the southern end of Kuda Bandos Falhu. Vegetated area of Kuda Bandos is approximately 3.27 hectares and island area is approximately 3.9 hectares. Total area of the reef where Kuda Bandos Island is situated is approximately 11.3 hectares and the total area of the reef flat is 5.8 hectares. After the proposed development the total built-up area of the island will be 7,450 m2 which is about 18% of the total land area of the island. Kuda Bandos Island has thick and healthy vegetation all around and inside the island. The canopy of the island is generally high all around the island except for the northern and western sides where a well-established vegetation mostly consisting of mature Funa, Dhigga, Magoo, Kuredhi, young Ruh, Boakashikeyo and Uni. In general, it can be estimated that the vegetation constituent of the island can be divided into around 50-55% Ruh, 20-25% trees such as Dhigga, Funa, Kaani, Uni, Magoo and Boakashikeyo and 15-20% comprising of introduced vegetation used for landscaping such as Saima, Kandholhu, Farudhaa Bageechaa, Croyton and others. Kuda Bandos is formed within its own coral reef system inside the atoll. The coral reef is triangular in shape and the island is found in the middle of the triangle in an egg-shape. This coral reef system has a perimeter of approximately 1.3km measuring from the outer reef edge. Kuda Bandos coral reef covers an area of approximately 7 hectares including the reef slope and the reef-flat. The general reef condition can be regarded as fairly good with increasing live coral cover of 12% on average and diversity towards the northern side of the reef. The lagoon system of Kuda Bandos has an average depth of 1 – 1.2m during high tide periods. It is a relatively small lagoon which is only found from north-east to the eastern side of the island having an approximate area of 8,745m2. The lagoon found on the north-west, west and south-western sides of the island are saturated with beach areas hence, very narrow areas of the lagoon were visible at the time of the assessments. During the preparation of the EIA report an impact matrix, which is a standard tool for identifying the possible impacts of project activities, has been created for proposed development project in Kuda Bandos Island. The activities carried out during the construction and post-construction or operational phases are arrayed against a selection of environmental factors that may be affected directly or indirectly as a result of project activities. The report has identified and described in detail possible change that would occur to the existing condition of the environment caused during the construction phase and have suggested appropriate mitigation measures for each and every impact identified in the report. Vegetation clearance has been identified as the most significant negative environmental impact that could be associated with the proposed development. Liquid, solid and other forms of wastes and particularly hazardous waste generated during the construction and operational phase has also been identified as significant impact associated with the project and appropriate mitigation measures are suggested for each and every waste related impact identified in the study. The study has evaluated alternative options for some components of the project and has suggested some modifications to the proposed layout based on the considerations given to the maximum land use and preserve the existing trees and minimise vegetation clearance which will have more impacts on the island. The report has come-up with an extensive monitoring programme that will keep on monitoring the environmental changes associated with the development and make necessary adjustment to the activities of the project based on the findings of various measured environmental parameters suggested in the monitoring plan. As part of the assigned tasks of EIA a list of stakeholders were provided in the TOR to undertake extensive stakeholder consolation during the EIA preparation process. This is because some concerns were raised by the media, soon after the Government’s decision to convert Kuda Bandos to a resort, stating that the island will be closed for local picnics after the development. The issue was discussed with the stakeholders and the truth about the misconception was cleared during the consultation. All the stakeholders except Malé City Council welcomed the proposed development. Malé City Council is on the opinion that Kuda Bandos is the only remaining island near Malé for the picnickers from Malé City and it is the only place where people of this congested city can go and take a breath of fresh air. Therefore they are in the opinion that resort development in Kuda Bandos should not go ahead and the island should be left as it is only for the picnickers from Malé despite the fact that the island will still be accessible for local picnickers after the proposed resort development. The following improvements for the facilities for picnickers and camping site in Kuda Bandos was suggested by the stakeholders during the discussions. 1. Increase the number of public toilets and improve the quality and maintenance 2. Provision of feeding rooms for babies 3. Increase the number of showerheads and properly maintain the water network 4. Increase the number of life guards and first aid facilities 5. Increase the number of guest rooms allocated for the Maldivians 6. Properly demark the picnic and tourist areas with appropriate signage The report has identified the following beneficial effects form resort development in Kuda Bandos:  Establishment of local tourism opportunities mixed with international tourism  Establishment of readily available picnic facilities and other amenities such BBQ pits, dining areas etc.  Increased direct employment and training opportunities;  Better guardianship of the terrestrial and marine resources of Kuda Bandos Island;  Improvements in environmental quality of the island;  Stimulation of local economy, cultivation and small business opportunities within the nearby island communities; and  Increased government revenue and increased GDP. The report found no evidence that the resort development in Kuda Bandos requires or involves any of the following environmental or socio-economic impacts.  loss of unique habitat or wilderness areas;  resettling of local communities;  removing or destroying cultural properties;  contravening national government of the Republic of Maldives, or island community policies, regulations, criteria, customs or aspirations concerning environment, economy, employment, cultural traditions or life styles. On the basis of this environmental impact assessment study and the impact mitigation measures proposed in the report will be duly implemented and recommendations are given due consideration, it is concluded that the benefits of the proposed resort development in Kuda Bandos will substantially outweigh its imposition on the environment.
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    Technical Report
    Environmental impact assessment for extension of Kooddoo Domestic Airport and development of a city hotel Kooddoo, GA. Atoll
    (2013-12) Adam, M. Shiham; Riyaz, Mahmood
    1. The domestic airport of Kooddoo was built during 2011 and was officially opened in 2011. This 1,200 m long airstrip in the north eastern side of the Ga Atoll serving the emerging high-end resorts have become one of the busiest and most important domestic airports in the south. It is normal to have 7-8 flights per day with mostly tourist passengers arriving and departing. Also relatively large volume local passengers make use of the route for transferring to the islands in the south or simply commuting on business trips. It was also noticed that guests with reputable business credentials were requesting to resort operators to allow their own air-craft (jet) to fly Kooddoo direct rather than having inconvenient and long layover times at Hulhule Ibrahim Nasir International Airport. 2. In order to address this need the Ministry of Tourism (previously Ministry of Tourism, Arts and Culture) engaged with the Maldives Civil Aviation Authority and the Ministry of Transport and Communication in a development project to extend the airstrip and also to upgrade and modernize the airport to provide services to international standards. Keong Hong Construction Pte Ltd, a reputable property developer in the region, won the airport development contract through competitive bidding tendered by the Ministry of Tourism. The negotiated contract agreement included development of a 50-room city hotel on Kooddoo and also development of Ga. Maamutaa as an upper-class tourist resort. Under the same agreement the Kooddoo airport will also be managed by Keong Hong Construction Pte Ltd, who now has an Aerodrome Certificate to run the airport under their name 3. Following the new Regulation on Reclamation and Dredging of Islands Lagoon and Reefs a permit for dredging and reclamation work was obtained before the scoping of the project took place. As such all paper works, including the dredging and reclamation permit was submitted for the Scoping Meeting held at EPA and was attended by stakeholders. 4. The scope of this development project is to reclaim about 260 m long and 150 m wide area from both ends of the island to extend the runway to 1,800 m, to dredge and create 500 m long entrance channel from the western corner of the reef connected to a harbour basin with access walkway jetty. The scope also includes the complete development works of the 50-room city hotel including upgrading of airport services and equipment following the expansion airport capacity. The most significant development activity with regards environmental change is the dredging of western side, reclamation of the both ends and development 25 over-water bungalows on the shallow lagoon on the western side. 5. Existing environmental conditions have been revised using the comprehensive set of baseline data gathered for the airport development project in 2011 but supplemented by additional field data gathered during the visit made in late November 2013. These have been used to assess and evaluate the environmental impacts from development activities. For activities with potential to cause significant impacts, appropriate and practical mitigation measures have been proposed. 6. Since management of Kooddoo airport is now under Keong Hong Construction Pte Ltd the plan is to upgrade and expand the utility services (production of water, generation of electrify and overhauling of sewerage system) to meet the additional requirements of the proposed city hotel. As such the developer plans to add on to the existing structures and arrangements as much as possible to cut down development costs and improve efficiency. 7. The developer pans to increase current water production capacity of 150 cubic meters per day to 450 cubic meters per day. This would involve installing and commissioning of 2 x 150 cubic meters day capacity RO plants. Electricity generation will be increased from its current capacity of 250kVA to 3110 kVA by adding 2x800 kVA units and 2x630 kVA units. The current septic sewerage system will be overhauled to modern Membrane Bioreactor (MBR) plant with a capacity to treat 200 cubic meters of sewage water per day The outflow water will have negligible amount of coliforms and so will be used for watering the plants and landscaping work. 8. Installation and commissioning of electricity generation and water production system will be done as per guidelines of the Maldives Energy Authority and Environmental Protection Agency respectively. Similarly, to ensure safety, drilling of boreholes for source water for RO plant and construction of 150,000 liters of fuel storage, and 20,000 liters of petrol will be stored in bunded areas. Environmental issues arising from these developments have been identified and practical mitigation measures have been proposed. It has been recommend that water production system and power generation system should be registered with the authorities before the its full commissioning. 9. Reclamation works and extension of runway will take place whilst the airport is in operation. In order to avoid disruption of flight schedules it is advised the developer/contractor provide method statements, including details on plans and schedule of activities that should be agreed in consultation with the Civil Aviation Authority. Coordination should be maintained at all times between the Air-traffic control tower and developer/contractor. Fortunately since the developer and airport management is the same company it is envisaged that there should not be any problems for this coordination. 10. The estimated volume of material recovered from dredging /excavation works is around 70,000 cubic meters. However, the estimated volume required for reclamation is estimated at 120,000 cubic meters. Alternative borrow areas have been identified to make up for this short fall. The issues were discussed at the Scoping Meeting and it was agreed that area on the south eastern side where the reef-flat is widest may be identified as a potential borrow area. Climate condition and orientation of the Kooddoo reef is such that lagoon often times becomes rough, thus prohibitive safe entry. As such hard structures (breakwaters) have been proposed for the channel and the harbor basin. 11. The proposed reclamation work on either end of the island extends close to the reef edge, creating the possibility of blocking the water exchange from the eastern and western side. It was noted that this may cause disruption of the established longshore drifts flow around the island creating areas of pockets of erosion and accretion. Since it will be difficult to predict such changes, appropriate environmental monitoring have been proposed. The developer/operator is encouraged to follow the monitoring programme and report to the authorities on a regular basis. Environmental monitoring allows detecting environmental change so that appropriate remedial action may be taken or addressed in a timely manner. 12. A Leopold Matrix has been used to classify the magnitude and importance of possible impacts which may arise during the constructional and operational phase of the project. Leopold Matrix is the most widely used methodology for identifying the impact of a project on the environment. It is a two dimensional matrix which cross references between the activities which are foreseen to have potential impacts on the environment and the existing conditions (environmental and social) which could be affected. It was concluded that the short term minor to moderate impacts as identified above outweigh the medium to long term socio-economic benefits to the region, to the tourism sector and to the country in general. 13. Since the Kooddoo Island is going to have three distinct business entities, namely Kooddoo Fisheries Maldives Ltd, Kooddoo Airport, and the Kooddoo City Hotel, the EIA report includes, an officially approved boundary demarcations in Annex 3.
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    Technical Report
    Environmental impact assessment for resort development in K. Kodhipparu, North Male Atoll
    (2014-04) Riyaz, Mahmood; Zuhair, Mohamed
    This is the Environmental Impact Assessment (EIA) report carried out for Kodhipparu Investment Pvt. Ltd to develop and operate a three star resort development in Kodhipparu Island located in North Malé Atoll. The proposed project includes development of 108 guest rooms and necessary infrastructure to establish and operate the resort in Kodhipparu Island. The EIA was prepared as fulfilment of the requirement by the Ministry Tourism (MoT) for granting permission for the project. Environmental Impact Assessment (EIA) of development projects is a requirement by the Environmental Protection and Preservation Act (EPPA) (law 4/93) of the Government of the Republic of Maldives. The total cost of the proposed project is approximately 15 million USD. The project will be developed within 18 months. The project will create a relatively large number of direct and indirect employment opportunities throughout the country. Therefore the project will significantly contribute to the economic growth, particularly tourism sector, and other relevant socio-economic activities This report has been prepared in accordance with the Environmental Impact Assessment Regulations published by the Ministry of Environment and Energy 2012 and covers both negative and positive environmental and socio-economic impact arising from the proposed project in Kodhipparu Island. Major findings of this report are based on information gathered during the field inspection of both the existing environment and possible effects of the project activities, through extensive literature review and experiences gained from similar projects elsewhere in the Maldives. The proposed project activity will take place in Kodhipparu Island (man-made island by accumulating sand through use of coastal structures and reclamation). The island lies on an irregular shape reef, with a deep lagoon at the center. Kodhipparu Island is located on the eastern end of the E-W oriented Kodhipparu Falhu on the southwestern side of North Malé Atoll. Kodhipparu being located on the southwester rim of the atoll it is exposed to high energy oceanic swells during the southwest monsoon and refracted, reflected and regenerated indirect fetch waves during the northeasterly monsoon. Due to the exposure of Kodhipparu reef to the direct oceanic waves during southwest monsoon the calmest area within the Falhu is on the eastern end. Hence Mr.Ali Fulhu who started constructing the island was aware that the eastern end of the reef is the most stable area with the least energy within Kodhipparu Falhu. The fact that Kodhipparu Island being a man-made island it does not have a proper soil layer with humus content. Most of the existing plant species are very young and introduced by the workers in order to stabilize the cay and hold sediments. Most of the vegetation consists of very basic salt and spray tolerant coastal plants, dominated mainly with, Scaevola sp. Tournafortia sp. Pemphis sp. and some coastal shrubs. Recently planted beach hibiscus, coconut trees, and Thespesia sp exist at the central part of the island. Love birds and parrots are being introduced and reared at the island in cages. Shorebirds and seabirds were known to visit the island. Two species of reptiles were observed, these were the mourning gecko (Lapidodactylus lugubris) and the garden lizard (Calotes versicolor). The overall reef of Kodhipparu reef is not in a good condition. Generally the live coral cover does not exceed 10% in any part of the surveyed area and consists of coral mainly branching and table corals. Percentage of dead coral was found to be very high 30-75% in most areas, particularly on the northern and northwestern side. The water in Kodhipparu is highly saline and not usable for washing or gardening. At present fresh water on the island is transported from Malé and supplemented by the rainwater catchments. During the preparation of the EIA report an impact matrix, which is a standard tool for identifying the possible impacts of project activities, has been created for proposed development project in Kodhipparu. The activities carried out during the construction and post-construction or operational phases are arrayed against a selection of environmental factors that may be affected directly or indirectly as a result of project activities. The report has identified and described in detail possible change that would occur to the existing condition of the environment caused during the construction phase and have suggested appropriate mitigation measures for each and every impact identified in the report. Sedimentation and increase in suspended sediment level in the water, has been identified as the most significant negative environmental impact that could be associated with the entrance clearance. Liquid, solid and other forms of wastes and particularly hazardous waste generated during the construction and operational phase has also been identified as significant impact associated with the project and appropriate mitigation measures are suggested for each and every waste related impact identified in the study. The study has evaluated alternative options for some components of the project and has suggested some modifications for resort layout and landscaping. Also the report found, based on the similar project activities elsewhere in the Maldives, the island and the reef will recover from the expected impacts rapidly and will re-establish a new ecological balance soon. However the report has come-up with an extensive monitoring programme that will keep on monitoring the environmental changes associated with the development and make necessary adjustment to the activities of the project based on the findings of various measured environmental parameters suggested in the monitoring plan. The report has identified the following beneficial effects form resort development in Kodhipparu:  Increased direct employment and training opportunities;  Better guardianship of the terrestrial and marine resources of Kodhipparu Island;  Improvements in environmental quality of the island;  Stimulation of local economy, cultivation and small business opportunities within the nearby island communities; and  Increased government revenue and increased GDP. The report found no evidence that the resort development in Kodhipparu requires or involves any of the following environmental or socio-economic impacts.  loss of unique habitat or wilderness areas;  resettling of local communities;  removing or destroying cultural properties;  contravening national government of the Republic of Maldives, or island community policies, regulations, criteria, customs or aspirations concerning environment, economy, employment, cultural traditions or life styles. On the basis this environmental impact assessment study and the impact mitigation measures proposed in the report will be duly implemented and recommendations are given due consideration, it is concluded that the benefits of the planned development in Kodhipparu Island will substantially outweigh its imposition on the environment.
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    Technical Report
    Environmental impact assessment for beach nourishment and maintenance dredging of access channels and harbour in Thulhaagiri Island
    (2014-01) Adam, M. Shiham; Riyaz, Mahmood
    1. Thulhaagiri is a small round island in the central North Malé Atoll. Located just north of Bandos Island resort, the island may be considered one of the oldest resorts in the Maldives, now operating for over 25 years. Currently in full operation, the resort has 52 beach bungalows and 34 over-water bungalows equipped with modern facilities and amenities. The current management of the resort is Angiri Resorts and Management Operation Pvt Ltd, which have been operating the resort for close to 15 years. 2. Owing to its somewhat isolated location in the centre of a large atoll basin, the island is exposed to wind driven waves from eastern and western side of the reef. Consequently the operators have been using two sides of the island for entry into the reef. During the SW monsoons season when winds are blowing from west the eastern entry is used and during north NE Monsoon when the winds are blowing from East and northwest the entry on the western side is used. 3. The inner reef flat used as a harbour sheltered by the well-developed reef crest. The area is shallow, but over time the reef flat becomes shallower due to deposition of sand. In order to maintain the depth at safer levels for the speedboats and vessels, a small pump is used to dredge the areas that get shallower. This has been the practice the resort operators. 4. The objective of the proposed project is to undertake maintenance dredging of the channels on the eastern and western side of the island and to deepen the reef flat area that is being used as harbour. And finally it is proposed to make use of the dredged sand to nourish the receding beaches on the north eastern side of the island. 5. The project activity is justified since these regular pumping and deepening of the channels and reef flat is inconvenient and hinders the smooth operation of the resort. During bad weather entry into the Thulhaagiri is dangerous and risky. There is also a need to rebuild the lost beach on the north-eastern side of the island, now felt necessary by the operators to maintain Thulhaagiri’s market position. 6. Following the recently established regulation on dredging and reclamation of the islands and lagoons, a permit was first obtained for the proposed reclamation and dredging followed by the scoping of the environmental impact assessment of these activities. This EIA is follows the Terms of Reference developed and agreed at the scoping meeting. 7. Dredging will be carried out by using a dredger mounted on a flat-top shallow-draft barge. A temporary sand bed may be constructed on the excavations area. Sand required for the construction of the bed will be obtained by excavation from the adjacent shallow areas. 8. Excavated material deposited on the barge will be transported and deposited on the beach identified for extending where it will be sieved. The coarse material will be deposited first for filling and extending the area followed the finer material on top. Temporary measures will be taken to avoid the sediment washing into the lagoon. Nourished beach will then be levelled using excavators, loaders or manually by the labourers. 9. It has been proposed that timing of this activity should be restricted to February and March, which is the transition period from northeast to southwest monsoon. Wind frequency and magnitude during the period is on the lower side. 10. The total time taken for this activity is estimated at 30 days following approval (or issuing of decision note) following successful evaluation of this report. The key mitigation measures other then timing is that limit dredging activity at lower or slack tide as much as possible. 11. The proponent has provided a commitment letter confirming accepting and confirming their responsibility on mitigation measures suggested in the report and environmental compliance during this undertaking of the proposed activities.