9      marine Ecology

9.1        Introduction

9.2        Environmental Legislation, Policies, Plans, Standards and Criteria

9.3        Assessment Methodology

9.4        Description of the Environment

9.5        Identification of Ecological Impacts

9.6        Evaluation of Ecological Impacts

9.7        Mitigation of Adverse Environmental Impact

9.8        Evaluation of Residual Impacts

9.9        Evaluation of Cumulative Impacts

9.10      Environmental Monitoring and Audit

9.11      Conclusion

9.12      References

 

 

 

 

9                    marine Ecology

9.1              Introduction

9.1.1        This section identifies and evaluates the nature and extent of potential impacts on marine ecological resources resulting from proposed dredging activities and other marine works in this designated project. Several relevant baseline studies and assessment reports are reviewed and both direct and indirect impacts on marine ecology during construction and operation phases are included in the assessment.

9.1.2        Where necessary, field surveys have been undertaken to check current ecological baseline conditions. Ecological importance of habitats and species potentially affected by proposed marine works are identified and assessed. The scale and significance of possible ecological impacts resulting from this designated project are evaluated, and necessary mitigation measures have been recommended. Residual and cumulative ecological impacts are also identified and evaluated, and ecological monitoring and audit requirements are discussed.

9.2              Environmental Legislation, Policies, Plans, Standards and Criteria

9.2.1        This section makes reference to the following HKSAR Government ordinances, regulations, standards, guidelines and documents when identifying ecological importance of habitats and species, evaluating and assessing potential impacts of the proposed development on the ecological resources:

·                     Environmental Impact Assessment Ordinance (EIAO) (Cap. 499) - aims to avoid, minimise and control the adverse effects on the environment by designated projects through the application of the environmental impact assessment process and the environmental permit system.

·                     EIAO Technical Memorandum on Environmental Impact Assessment Process (EIAO-TM) Annex 8 – provides guidelines for the evaluation of the ecological impact caused by the designated project. A list of criteria is provided for assessing the importance of habitat / species and the ecological impact.

·                     EIAO-TM Annex 16 – describes the general approach and methodology for assessment of ecological impacts arising from a project or proposal, to allow a complete and objective identification, prediction and evaluation of the potential ecological impacts.

·                     EIAO Guidance Note No. 3/2002 - provides guiding principles on the approach to assess the recommended environmental mitigation measures in Environmental Impact Assessment (EIA) reports.

·                     EIAO Guidance Note No. 6/2002 - provides some guidance on conducting ecological assessment.

·                     EIAO Guidance Note No. 11/2004 - introduces some general methodologies for marine ecological baseline surveys.

·                     Wild Animals Protection Ordinance (Cap. 170) - designated wild animals are protected from being hunted, whilst their nests and eggs are protected from injury, destruction and removal.  All birds and most mammals, including marine cetaceans, are protected under this Ordinance. The Second Schedule of the Ordinance, which lists all the animals protected, was last revised in June 1997.

 

·                     Protection of Endangered Species of Animals and Plants Ordinance (Cap. 586) – to give effect to the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES), the Ordinance strictly regulates the import, introduction from the sea, export, re-export and possession or control of certain endangered species of animals and plants and derivatives of those species scheduled in Appendices I, II and III. The Ordinance came into effect on 1 December 2006.

·                     Town Planning Ordinance (Cap.131) - provides for the designation of coastal protection areas, Sites of Special Scientific Interest (SSSIs), Conservation Area, Country Park, Green Belt or other specified uses that promote conservation or protection of the environment.

·                     The Marine Parks Ordinance (Cap.476) and Subsidiary Legislation - allows for designation, control and management of marine parks and marine reserves through regulation of activities therein to protect, conserve and enhance the marine environment for the purposes of nature conservation, education, scientific research and recreation. The Ordinance came into effect on 1 June 1995.

·                     The Protection of the Harbour Ordinance (Cap.531) – bases on a presumption against reclamation, the harbour is to be protected and preserved as a special public asset and a natural heritage of Hong Kong people.

·                     The Water Pollution Control Ordinance (Cap.358) – aims to control water pollution in waters of Hong Kong. Water control zones are designated with individual water quality objective to promote the conservation and best use of those waters in the public interest. The most updated water quality objective for the Victoria Harbour Water Control Zone was revised in June 1997.

9.2.2        This section also makes reference to the following international conventions and nearby national regulation:

·                     International Union for Conservation of Nature and Natural Resources (IUCN) 2006 Red Data Books - provides taxonomic, conservation status and distribution information on threatened species that have been evaluated using the IUCN Red List Categories and Criteria. This system is designed to determine the relative risk of extinction, and the main purpose of the IUCN Red List is to catalogue and highlight those taxa that are facing a higher risk of global extinction.

·                     The PRC National Protection Lists of Important Wild Animals and Plants - lists detailed Category I and Category II key protected animal and plant species under Mainland Chinese Legislation. The list was last updated in November 2002.

9.3              Assessment Methodology

9.3.1        Proposed dredging activities for the installation of the new cross harbour watermains would affect part of the existing shoreline and seabed at Wan Chai District near the HKCEC. In general, the boundary of the Assessment Area is 500 m from the proposed work area. The marine ecological environment of the Assessment Area, as shown in Figure 9.1, comprises largely the Victoria Harbour extending from Wan Chai to North Point, including the Causeway Bay Typhoon Shelter (CBTS).


Literature review

9.3.2        The assessment of ecological impact on marine habitats has been undertaken with reference to the previous baseline surveys and EIA studies for other proposed projects in and within the vicinity of the Assessment Area. These include the following:

·                     Central Reclamation Phase III Studies - Site Investigation, Design and Construction. Comprehensive Feasibility Study for Minimum Option: Final Key issues and Initial Environmental Impact Assessment Report (CRIII EIA report).

·                     Agreement No. CE 52/95, Strategic Sewage Disposal Scheme Environmental Impact Assessment Study (SSDS EIA study).

·                     Agreement No. CE 74/98, Wan Chai Development Phase II Comprehensive Feasibility Study (WDII EIA report).

·                     Agreement No. CE 42/2001, Environmental and Engineering Feasibility Assessment Studies in Relation to the Way Forward of the Harbour Area Treatment Scheme – Water Quality, Ecological and Fisheries Impact Assessment (HATS EEFS report).

·                     Agreement No. CE 25/2002, Drainage Improvement in Northern Hong Kong Island – Hong Kong West Drainage Tunnel Environmental Impact Assessment Final Report.

·                     CityU Professional Services (2003) Consultancy Study on Marine Benthic Communities in Hong Kong. Final Summer Field Survey Report. Submitted to AFCD.

·                     EPD Water Quality in Hong Kong 2004.

·                     AFCD Port Survey 2001-2002.

·                     Agriculture, Fisheries and Conservation Department, 2004. Ecological Status and Revised Species Records of Hong Kong’s Scleractinian Corals. Hong Kong: Agriculture, Fisheries and Conservation Department, HKSAR.

·                     Alan L.K. Chan, Choyce L.S. Choi, Denise McCorry, Khaki K., Chan, M.W. Lee and Ang Put Jr. 2005. Field Guide to Hard Corals of Hong Kong. 1st Edition (Eds. W.C. Chan and Edward Stokes). Friends of the Country Parks and Cosmos Book Ltd, Hong Kong.

Ecological surveys

9.3.3        Field surveys are considered necessary, where appropriate, to supplement and check the validity of data collected through the literature review process.  The field surveys for this assessment include:

·                     Ecological survey on intertidal and benthic habitats in the Assessment Area was conducted in January 2007. The survey included spot-check reconnaissance dives on 29 representative line transects and Rapid Ecological Assessment (REA) (DeVantier et al., 1998) at two spot-check sites where signs of coral colonies were first observed during the spot-check dives.  Detailed survey plan and methodology were presented in the Dive Survey Report (Appendix 9.1);


·                     Intertidal communities surveys on artificial intertidal habitats within the Assessment Area were conducted in August 2006 by direct observation along the shoreline. Fauna species and relative abundance were recorded and identified according to Williams (2003). In addition, the natural coastline at the northern part of Kellett Island was surveyed in January 2007 for the intertidal assemblage using standard transect method. Detailed survey plan and methodology were presented in the Intertidal Survey Report (Appendix 9.2).

·                     Avifaunal survey was conducted in area of Victoria Harbour and CBTS during August 2006 by fixed point direct observation (sight and call). Identification of bird species was made reference to Viney et al. 2005;

Impact assessment methodology

9.3.4        Evaluation and assessment of potential impact on ecological resources was conducted in accordance with the criteria and guidelines specified in Annex 8 and Annex 16, respectively, of the EIAO-TM.

9.3.5        The significance of impacts was ranked as “low”, “moderate” or “high” based on the criteria shown in Table 9.1.  The description of the ranking is as below:

9.3.6        Low - Impacts to species or groups are assessed as “low” if the predicted impact would result in a slight, and / or short-term reduction in the local population numbers or geographic distribution of a species or group, but the species or group is predicted to recover from the perturbation with no-long term adverse impacts.  Impacts to habitat are assessed as “low” when the habitat is widely distributed locally and that no rare or restricted species are found in the habitat.

9.3.7        Moderate – Impacts to species or groups are considered “moderate” if the predicted impact probably would result in non-recoverable and / or long-term reduction in population numbers.  However, the species in question should be considered widely distributed or common, and abundant on a local, regional or global scale.  Impacts to habitat are assessed as “moderate” if the habitat is of limited local or regional distribution or declining in extent and that the habitat has a potential of supporting fauna and / or fauna of conservation importance.

9.3.8        High – Impacts to species or groups are judged to be “high” if the predicted impact has an adverse effect on species or groups which are rare, protected or of conservation importance locally, regionally, or globally.  Impacts to habitat are considered to be “high” if the habitat in question is of limited local or regional distribution or declining in extent and that it is generally considered by the scientific community to be of local, regional or global importance to the support of rare or restricted flora and /or fauna species.

9.3.9        If impacts on ecological resources are found to be significant (that is, moderate or high), mitigation measures would be recommended in accordance with the EIAO-TM Annex 16 and EIAO Guidance Note No. 3/2002.  Impact mitigation would be sought in the following priority: avoidance, minimisation, on-site compensation and off-site compensation.

9.3.10    Impact avoidance generally consists of modifications to the preferred development options, but may in some extreme cases require abandonment of the project. 

9.3.11    Impact minimisation includes any means of reducing the scope or severity of a given impact, for example, through timing of construction programme, modification in the design or ecological restoration of disturbed areas following the completion of works. 

9.3.12    Impact compensation will be recommended if the effect on a given species or habitat is irreversible and attempts will be made to compensate it elsewhere, for example, enhancement, creation of suitable habitats or recreation of the habitat.  Compensation can be on-site or off-site.

9.4              Description of the Environment

9.4.1        The marine environment in the Assessment Area is composed of the coastal water of Victoria Harbour and the Causeway Bay Typhoon Shelter (CBTS). Representative photographs of marine environments are given in Appendix 9.3. In general, these two areas are similar in water quality and sediment contamination as they are hydrographically interconnected with each other. However, as CBTS is located within an embayment with limited flushing, it is more vulnerable to pollution than the coastal water in Victoria Harbour.

            Area of conservation interest

9.4.2        There are no ecological sensitive receivers, such as SSSIs, Marine Parks/Reserves or other areas of ecological importance or conservation interest, in and within the vicinity of the Assessment Area.  As the proposed marine works will include dredging activities, far-field ecological sensitive receivers have been identified. These potential off-site ecological sensitive receivers include coral area located at Green Island, Little Green Island (6 km) and Junk Bay (8 km).

Abiotic

Water

9.4.3        Under the Water Pollution Control Ordinance (Cap. 358), the Victoria Harbour is within the gazetted Victoria Harbour Water Control Zone. In the previous WDII EIA report (Maunsell, 2001), marine water in the Victoria Harbour was identified as turbid, hypoxic and highly eutrophic, that was due to the direct discharge of wastewater into the harbour area with only preliminary treatment for the discharged sewage (screening).

9.4.4        However, after the commissioning of the Stonecutters Island Sewage Treatment Works (SCISTW) in 2002 under stage 1 of the Harbour Area Treatment Scheme (HATS), water quality has improved significantly, especially in the eastern harbour area. According to the EPD’s water quality monitoring results, marine water in the Assessment Area (Station VM4 and VM5) is now less turbid (turbidity 6.7-12.6 NTU), more oxygenated (dissolved oxygen 3.9-7.5 mg L-1), and lower in inorganic nutrients (total nitrogen 0.14-0.61 mg L-1 and total phosphorus 0.02-0.08 mg L-1) (EPD, 2005).

9.4.5        However, the levels of E. coli (510-15000 cfu per 100 mL) and faecal coliforms (2100-34000 cfu per 100 mL) increased substantially over the decade, indicating increasing faecal contamination (EPD, 2005).

9.4.6        In general, water quality in the Assessment Area has been improved recently but the Victoria Harbour provides a relatively poor marine habitat compared to eastern and southern waters in Hong Kong.      


Sediment

9.4.7        The seabed in the Assessment Area is mainly composed of soft bottom sediment with coarse particle size. The marine sediment in Victoria Harbour, according to EPD’s monitoring results, is highly anaerobic (electrochemical potential -409mV to -258 mV) due to high organic loading from sewage over the years. The sediment is toxic with high level of ammonia nitrogen (15-86 mg L-1) and total sulphide (170-1700 mg kg-1). It is also highly contaminated with copper (84-250 mg/kg) and silver (3.0-11 mg/kg) which exceed the Lower Chemical Exceedance Level (LCEL) or Upper Chemical Exceedance Level (UCEL), as defined in the ETWB Technical Circular (Works) No. 34/2002 (EPD, 2005).

9.4.8        Previous WDII EIA Report (Maunsell, 2001) pointed out that numerous ecological studies have been conducted in the Victoria Habour, and those have usually determined its polluted nature using single species or indicator groups (e.g. barnacles, Chan et al., 1990; Rainbow and Smith, 1992; Blackmore, 1999; fish, Kwan, 1999 and mussel, Nicholson, 1999). 

9.4.9        A recent sediment toxicity test was carried out under the HATS EEFS study and sediments collected from Victoria Harbour (Station XN4 and VM7) were highly toxic to benthic amphipod Leptocheirus plumulosus, resulting in very low survivalship of 9-31% only (CDM, 2004).

Biotic

9.4.10    The Assessment Area comprises several broad marine habitats including:

·                     Benthic habitat on soft bottom substratum of the Victoria Harbour.

·                     Intertidal habitats on artificial seawall and mimic rocky shore.

·                     Intertidal habitats on natural rocky shore of northern Kellett Island.

·                     Subtidal habitat in Victoria Harbour.

·                     Feeding ground for waterbirds in CBTS near A King Shipyard.

9.4.11    Representative photographs of some identified marine habitats are presented in Appendix 9.4. The baseline ecological conditions of different marine habitats in the Assessment Area are described below.

Soft bottom benthos

9.4.12    Previous WDII EIA report summarised the findings in Thompson and Shin (1983) and showed that benthic assemblages in the Assessment Area were typically of low diversity and abundance, and community structure was largely dictated by organic pollution from sewage discharges in the past.  As only a limited number of hypoxia tolerant species can survive the bottom conditions within the study area region, fauna was dominated by opportunists such as bivalves and polychaetes.

9.4.13    Dominant polychaetes include Minuspio cirrifera and the best-known marine organic enrichment indicator Capitella capitata.  These polychaetes may be indicators of moderate and severe organic pollution, respectively. The moderately pollution tolerant bivalve Ruditapes philippinarum (stated as Tapes philippinarum) was also found dominant in the benthic infaunal population in the same study (Thompson and Shin, 1983).


9.4.14    Another field survey of soft bottom benthic organisms at the seabed in the Victoria Harbour near the Central District conducted for CRIII EIA Study (Atkins China Ltd., 1999) was also reviewed in previous assessment. This field survey indicated that the soft bottom marine environment in the Victoria Harbour was polluted and lacked a macroinvertebrate community.

9.4.15    The field survey carried out for the SSDS EIA study also confirmed a very low species diversity and evenness for benthic assemblages in Victoria Harbour and was indicative of stressful environment for benthos (Binhai, 2000).

9.4.16    A recent study on marine benthic communities in Hong Kong showed that a coarser sediment benthic group was found in Victoria Harbour (Station 53 & 54) as compared to eastern and southern waters, with lower species diversity and evenness resulted (CityU, 2002).

 

9.4.17    This study showed that the benthic communities in Victoria Harbour comprised of mainly polychaete (Cirratulus sp., Schistomeringo rudolphi, Dodecaceria sp., Naineris sp., Sigambra hanaoka and Prionospio sp.), oligochaete (Thalassodrilides gurwitchi), bivalve (Ruditapes philippinarum) and crustacean (amphipod Cheiriphotis megacheles) (CityU, 2002). It indicated a distinct benthic composition which is characterized by species strongly adaptable to eutrophic environment.

9.4.18    Other recent survey for HATS EEFS study on benthic assemblages in Victoria Harbour near North Point (Station VM2 and XM4) also indicated that the benthic assemblage was dominated by polychaeta (Naineris sp., Glycera sp., Prionospio sp.), mollusca (Ruditapes sp.) and crustacea (Corophium sp.). Bivalve Ruditapes sp. is the most abundant (44%) fauna, comprising 95% of the whole benthic assemblage biomass. Although it is a commercial species, the conservation value is not high. It was noted that the benthic community structure has been relatively stable over the years and so quite robust to environmental disturbance (CDM, 2004).

 

Intertidal Communities (Artificial)

9.4.19    Intertidal seashore habitats in the Assessment Area mostly comprise of the artificial vertical seawalls, with small portion of man-made sloping seawalls and rockfills (rocky shores ‘mimic’ natural habitat) at the Wan Chai Ferry Pier and around the HKCEC.

9.4.20    Previous WDII assessment reviewed a number of literatures and indicated that fauna presented in seawalls and rockfills were largely restricted to encrusting sessile organisms such as bivalves, molluscs and barnacles (Morton and Morton, 1983; Lee, 1985; Lee and Morton, 1985). 

9.4.21    Fauna commonly encountered included molluscs such as the common neogastropod (Thais clavigera) and the pollution-tolerant bivalve (Perna viridis), as well as encrusting crustaceans such as barnacles (Balanus spp., Tetraclita squamosa and Capitulum mitella) and the ubiquitous mobile isopod (Ligia exotica) (Morton and Morton, 1983; Lee, 1985; Lee and Morton, 1985).

9.4.22    Flora is mostly restricted to algae that are either organic or nutrient enrichment indicators such as Ulva spp. and Cladophora (Morton and Morton, 1983; Ho, 1987; Moore, 1990).

9.4.23    A recent intertidal fauna survey on artificial seawalls and rockfills within the Assessment Area was carried out in August 2006 to confirm the validity of the literature results. The list of intertidal fauna is summarised in Appendix 9.5. Compared to the past records, similar biotic assemblages on artificial intertidal habitats around HKCEC, CBTS and the shoreline of City Garden in North Point were found in current survey and the intertidal composition in the Assessment Area was generally consistent with the past recorded results.

9.4.24    The artificial seawalls in the Assessment Area were found to be generally inhabited densely by few species of sessile encrusting fauna, including chiton (Acanthopleura japonica), barnacle (Tetraclita squamosa) and bivalve (Saccostrea cucullata). The only mobile species found on the artificial seawalls were the common Sea Slater (Ligia exotica) and topshell (Monodonta labio). All of them are common local intertidal species with low conservation interest.

9.4.25    It was found that the mimic rocky shores located at the Wan Chai Ferry Pier and the shoreline of the HKCEC provided a more diverse and abundant intertidal community compared with the vertical and sloping seawalls. Limpet (Patelloida saccharina) and small crab, together with the species described in 9.4.23, were recorded in the rockfill habitats.

9.4.26    In the current study, encrusting algae (Pseudulvella applanata and Hildenbrandia sp.) were recorded on the surface of artificial vertical seawalls in the Assessment Area. No erect algae or higher flowering plant was found during the recent survey.

Intertidal Communities (natural)

9.4.27    Part of the coastline found at the northern part of the Kellett Island is the only natural coastline within the study area. The natural coastline on Kellett Island is a typical sheltered rocky shore subjected to only slight wave action.

9.4.28    Field survey conducted for the WDII EIA study indicated that the sheltered rocky shore communities were composed of large quantities of topshell (Monodonta austrailis) dominating the lower shore and periwinkles (Nodilittorina millegrana), dominating the upper shore (Maunsell, 2001). 

9.4.29    Other intertidal species including Stalked Barnacle (Pollicipes mitelia), Acorn Barnacle, (Tetraclita squamosa), common chiton (Liolophura japonica) and limpet (Cellana toreuma) were occasionally observed.  In general, the species diversity and abundance were relatively low compared to other natural shoreline in Hong Kong. No rare species or species of conservation value were observed in this survey (Maunsell, 2001). 

9.4.30    A recent intertidal survey on the shoreline of northern Kellet Island was conducted in January 2007 in order to provide more detailed and updated information on the existing ecological assemblage profile in this natural habitat. Detailed survey methodology, location, result and discussion are provided in the Intertidal Survey Report (Appendix 9.2). Figure 1 of the Appendix 9.2 indicates the two surveyed locations within the natural shoreline where quadrats of 0.5 m x 0.5 m dimension were laid at 1 m interval along 10 m transects which extended from high tide mark to low tide mark. Epifauna within each quadrats were identified, enumerated and recorded.

9.4.31    Recent survey revealed that natural coastline at the northern Kellet Island was limited to small area of less than 20 m x 100 m dimension only with natural substrata of large boulders, cobbles and bedrocks and some old concretes. The nearby intertidal habitats were mainly composed of artificial seawalls and rock armours and this habitat was subjected to high level of disturbance from past construction and reclamation works at nearby areas.

9.4.32    A total of seven species were recorded during recent survey and their abundances were shown in Table 1 of Appendix 9.2. Similar composition and distribution pattern of intertidal communities were observed during recent survey compared with those reported in WDII EIA Study. Periwinkles (Nodilittorina millegrana) and topshell (Monodonta austrailis) were the most common species recorded on both transects with N. millegrana dominating the upper shore and M. austrailis dominating the lower shore. Other intertidal species including limpet (Cellana toreuma), Nerite (Nerita chanaeleon), Stalked Barnacle (Capitulum mitella) and Acorn barnacle (Tetraclita squamosa) were also recorded. All the recorded species are common in most of the shorelines in Hong Kong and no species of conservation importance or nursery/breeding activities was observed in this area.

Subtidal fauna

Marine mammals

9.4.33    Literature review has shown that there were no sightings of marine mammals within the Assessment Area. One of the most important marine mammals in Hong Kong waters is the Chinese White Dolphin (Sousa chinensis) which was only seen in the western estuarine waters in Hong Kong including outer Deep Bay, north, south, east Lantau and west Lamma (Hung, 2006). The other common marine mammal Finless porpoise (Neophocaena phocaenoides) was also never reported in the Victoria Harbour and only occurs in the eastern and southern waters of Hong Kong (Jefferson, 2001). There is no significant record of such marine mammals with high conservation interest within the Assessment Area.

            Corals

9.4.34    In Hong Kong, the richest coral communities are found in the eastern part where water is free from the influence of estuarine water from the Pearl River. As water in Victoria Harbour was turbid with high level of suspended solids, it was unsuitable for coral to survive and colonise there.  Based on the review on a number of previous literatures, there was no significant record of coral reported within the Assessment Area.

9.4.35    Literature review indicated that the nearest soft corals and gorgonians are located at Green Island and Little Green Island about 6 km west from the reclamation area. A low coverage of black coral of Anthipathes sp. was also found in Green Island (TDD, 1998). In general, soft coral and gorgonians are more resistant to turbid waters than hard coral as they do not contain symbiotic algae zooxanthallae and do not require light penetration for photosynthesis.  Therefore, they are more widely distributed in Hong Kong and are also found in areas of higher turbidity.

9.4.36    The EIA study for Tseung Kwan O Further Development also identified the presence of small colonies of hard corals with sparse cover of soft corals and gorgonians found in Chiu Keng Wan located at the northwestern Junk Bay, which is about 8 km to the east from the Project area (Maunsell, 2005).

9.4.37    Recent dive survey for HATS EEFS Study also indicated that the shallow water of Joss House Bay and north-west Tung Lung Chau (over 10 m east of the reclamation area) supported reasonably diverse but low cover hard coral communities. However, the same study showed that there were no hard corals or soft corals observed in the North Point areas (CDM, 2004).

9.4.38    Due to lack of information on presence of coral communities in and within the Assessment Area, recent dive survey was carried out during January 2007 in order to provide sufficient and updated information for the evaluation of any potential impact to coral arising from the proposed marine works. Details on the methodology, surveyed area, results, discussion and recommendation are provided in the Dive Survey Report (Appendix 9.1).

9.4.39    Spot-check reconnaissance dives were first conducted to identify the extent of hard substrate with an emphasis on gaining an overview of coral occurrence within and adjacent to the proposed reclamation area. Areas with corals identified in spot-check dives were then further surveyed using REA technique along 100 m transect. Figure 1 & 2 of Appendix 9.1 indicate the areas covered by the spot-check dives and the locations where the REA transects deployed.

9.4.40    As illustrated in Table 2 of Appendix 9.1, 29 representative line transects of totally 4680 m were surveyed in spot-check dives. The underwater visibility at all surveyed sites were generally poor (< 2 m). The maximum water depth in all the surveyed sites ranged from 3 m to 8 m. Bottom substrata were mainly composed of muddy or sandy seabed with hard substrata rubble seawalls for most of the surveyed sites while rock or boulder was also found at Site 3, 6, 13, 14 and 18-21.

9.4.41    In all of the surveyed sites, the seabed quality is generally poor with limited marine life observed. Only one species of hard coral (Oulastrea crispata) and one species of octocoral (gorgonian Echinomuricea sp.) were found at Site 13 and Site 27 respectively. But they are all small in size, sparsely distributed and in very low coverage (< 1%). Neither soft coral nor black coral was identified during the spot-check dives.

9.4.42    More detailed REA surveys were then carried out at Site 13 and Site 27. Substrata at Site 13 were mainly composed of muddy and sandy bottom with boulders while Site 27 comprised muddy bottom with hard substrata of rubber seawalls.

9.4.43    At site 13, only sparse coverage (1-5%) of totally 18 colonies of single hard coral species (Oulastrea crispata) was recorded during the REA survey. Most of the colonies were attached on the small rocks or boulders less than 50 cm in diameter in the ex-Public Cargo working Area (PCWA) basin near the pier of the Hong Kong Yacht Club. All the colonies found at Site 13 were in fair health condition but in small size ranged from 3 cm to 8 cm in diameter. Oulastrea crispata has a wide range of adaptations to different environmental conditions (including those unfavourable to corals) as well as geographic locations, which is a result of its stress-tolerant ability (Chen, et al. 2003). With an opportunistic life history trait, a wide range of reproductive strategies and surface-orientation independent growth, O. crispata is able to colonise a variety of substrata and to flourish as a pioneer coloniser of newly immersed structures (Lam, 2000a & 2000b). It is common and widespread in Hong Kong marine waters, especially those more turbid and harsh environment in the western waters (Chan, et al. 2005).

9.4.44    Very low coverage (1-5%) of only one colony of octocoral (gorgonian Echinomuricea sp.) was found at Site 27 during the REA survey. It was located on the seawall at North Point Shoreline next to a public pier which is about 250 m away from the CBTS. The colony found was small in size (25 cm in diameter) and in fair condition. Echinomuricea sp. is a common gorgonian coral found in Hong Kong water, especially in those turbid waters at southern and western part of Hong Kong.

 

Feeding ground in CBTS

9.4.45    Recent avifaunal survey revealed few bird species presented in the Assessment Area and list of birds was summarised in Appendix 9.6. The locations of species of conservation interest recorded in the Assessment Area were indicated in Figure 9.1.

9.4.46    It was found that CBTS, particularly the area near the A King Shipyard, is a feeding ground for ardeids of conservation interest including Little Egret (Egretta garzetta), Great Egret (Ardea alba) and Black-crowned Night Heron (Nycticorax nycticorax). The other species of conservation interest found during recent survey included the White-throated Kingfisher (Halcyon smyrnensis) and Black Kite (Milvus migrans). All wild birds are protected under the Wild Animals Protection Ordinance (Cap, 170) and the conservation status of the recorded species of conservation interest is discussed in details below.

9.4.47    A total of 36 Little Egret (Egretta garzetta) was found foraging and feeding in the coastal water of Victoria Harbour and CBTS. Although Little Egret is a common ardeid which is widely distributed in the coastal waters throughout Hong Kong, it is considered to be a species of conservation interest regionally due to its restricted site of breeding and roosting (Fellowes et al., 2002).

9.4.48    A Great Egret (Ardea alba) was also observed forage and feed together with the Little Egret population at the CBTS near A King Shipyard. Although this species is a common resident and winter visitor in Hong Kong, the Great Egret is considered to be of conservation interest regionally due to its restricted breeding and roosting area (Fellowes et al., 2002).


9.4.49    Six Black-crowned Night Heron (Nycticorax nycticorax) (including one juvenile) were also recorded foraging and feeding at the CBTS near A King Shipyard. This ardeid is a common local resident and winter visitor in Hong Kong. Due to its restricted breeding and roosting area, it is listed as a species of conservation interest locally (Fellowes et al., 2002).

9.4.50    A total of four Black Kite (Milvus migrans) was observed at flight above the Victoria Harbour and CBTS during recent survey. This species is a common resident and winter visitor in Hong Kong (Carey et al., 2001). Black Kite is a Category II protected species under Mainland Chinese Legislation. Although locally very common, Kites are considered as species of conservation interest regionally due to its restricted number of nesting and roosting sites (Fellowes et al., 2002), with the current breeding population believed to be about 30 pairs (Carey et al., 2001).

9.4.51    A White-throated Kingfisher (Halcyon smyrnensis) was recorded in the CBTS near A King Shipyard. This species is a local common resident and is widely distributed in the coastal areas throughout Hong Kong (Carey et al. 2001). It is listed as species of conservation interest locally due to its restricted breeding and roosting site (Fellowes et al. 2002).

Ecological Importance

9.4.52    Based on the available literature and discussion presented above, the ecological values of marine resources present within the Assessment Area have been assessed and evaluated. This has been determined in accordance with the EIAO-TM Annex 8 Table 2 criteria and is shown in Tables 9.1.


Table 9.1         Criteria and Evaluation of Ecological Importance of Marine Habitats in the Assessment Area.

Criteria

Soft bottom habitat

Intertidal habitat (artificial)

Intertidal habitats (natural)

Subtidal

habitat

Feeding ground in CBTS

Naturalness

Subjected to extensive anthropogenic disturbance

Man-made habitat

Basically natural but its naturalness were partially affected by past reclamation and construction.

Highly disturbed by marine traffic, subjected to extensive water pollution

 

Disturbed by marine traffic and human activities

Size

Large, 15 ha

Large, 1 km long

Small, less than 100 m long

Large, 15 ha

Large, 16 ha

Diversity

Low, mainly dominant by pollution-tolerant fauna

Low, mainly composed of few intertidal fauna

Low, mainly composed of few intertidal fauna

Low, species confined to those resistant to polluted water

Low, only few avifaunal species found

Rarity

No rare species found

No rare species found

No rare species found.  But this coastline is one of the remaining natural habitats on the north shore of Hong Kong Island

No rare species found but only one species of common hard coral and one species of common gorgonian were recorded

No rare species recorded but species of conservation interest including Little Egret, Great Egret, Black-crowned Night Heron, Black Kite and White-throated Kingfisher were found

Re-creatability

High

Very High

Moderate

High

High

Fragmentation

The habitat is not fragmented.

The habitat is highly fragmented.

The habitat is fragmented.

The habitat is not fragmented.

The habitat is not fragmented.

Ecological linkage

Not functionally linked to any highly valued habitat in close proximity.

Not functionally linked to any highly valued habitat in close proximity.

Not functionally linked to any highly valued habitat in close proximity.

Not functionally linked to any highly valued habitat in close proximity.

Not functionally linked to any highly valued habitat in close proximity.

Potential value

Very low

Very low

Low

Low

Low

Nursery ground

No significant record.

No significant record.

No significant record.

No significant record.

No significant record.

Age

NA

NA

NA

NA

NA

Abundance / Richness of wildlife

Low for abundance and species richness

High for abundance but low for species richness

High for abundance but low for species richness

Low for abundance and species richness

Low for abundance and species richness

Ecological importance

Very low

Very low

Low

Low

Low

 

9.4.53    Species of conservation interest recorded in the Assessment Area are evaluated in Table 9.2 below

Table 9.2         Species of Conservation Interests recorded in the Assessment Area.

Species

Location

Protected

Status 1

Distribution & Rarity 2

Coral

Hard coral

Oulastrea crispata

Ex-PCWA Basin near the pier of the Hong Kong Yacht Club

Listed in Cap. 586

Common in Hong Kong waters.

Gorgonian Echinomuricea sp.

Seawall next to a public pier which is about 250 m away from the CBTS

-

Common in Hong Kong waters.

Avifauna

Black-crowned

Night Heron

Nycticorax nycticorax

CBTS near A King Shipyard

-

Locally common, but with limited number of breeding sites in Hong Kong. Local concerned conservation species.

Little Egret

Egretta garzetta

CBTS near A King Shipyard and the Victoria Harbour

Listed in Cap. 586

Locally common, but with regional concerned conservation interest for its restricted breeding sites in regional area.

Great Egret

Ardea alba

CBTS near A King Shipyard

Listed in Cap. 586

Locally common, but with regional concerned conservation interest for its restricted breeding sites in regional area.

White-throated Kingfisher

Halcyon smyrnensis

CBTS near A King Shipyard

-

Common resident in Hong Kong, but is local concerned conservation species for its restricted breeding site recorded.

Black Kite

Milvus migrans

CBTS near A King Shipyard and the Victoria Harbour

Listed in Cap.586 and Category II protected species under Mainland national legislation

Common resident and winter visitor in Hong Kong. Regional concerned conservation species.

 

Note 1: All wild birds in Hong Kong are protected under Ordinance Cap.170

Note 2: Information taken from various sources including Viney et al. (2005), Carey et al. (2001), Fellowes et al. (2002) and Chan et al. (2005).

 


9.4.54       Soft bottom seabed and artificial interidal habitat are considered as very low ecological importance. This is based on the considerations of their highly disturbed nature, low species diversity and absence of rare species found in current ecological impact assessment.

9.4.55       Ecological value of natural intertidal habitat found in northern coastline of Kellet Island is ranked of low level due to its small size, low species richness and partial loss of naturalness by past reclamation and construction works, though it is scarce natural intertidal habitat existing in the northern Hong Kong Island.

9.4.56       The colonies of hard coral and gorgonian found in the subtidal habitat are low in species richness and abundance, small in size and they are common species which can tolerant to more turbid water and can be found in many locations of Hong Kong waters. In view of the poor habitat quality (e.g. high SS level, low light intensity, etc) for coral colonization compared with other locations in Hong Kong waters, the subtidal habitat is considered as low in ecological importance.

9.4.57       Although feeding ground in CBTS serves as a foraging area for some waterbirds and other avifaunal species of conservation interest in local or regional area due to their restricted breeding number and site recorded, the habitat size, species diversity and abundance are relatively low. Similar alternative feeding grounds for ardeids and other bird species of conservation interest  are also found available in the vicinity such as the Kwun Tong Typhoon Shelter, To Kwa Wan Typhoon Shelter and Yau Ma Tei Typhoon Shelter. Therefore, this habitat is not considered as an important feeding ground for the bird population and its ecological significance is ranked as low.

 

9.5              Identification of Ecological Impacts

9.5.1        Impacts to marine ecological resources may occur during the construction phase. The impacts may be derived from direct loss of habitats or indirect disturbance through changes to key water quality parameters and increased levels of background noise and marine traffic.

Construction phase

            Direct impact

9.5.2        Potential direct impacts on marine ecology arising from the proposed marine works would include loss of habitats and the associated marine species due to dredging activities. This would include temporary loss of small areas (less than 0.5 hectare) of soft bottom seabed and subtidal habitat along the alignment of the new cross harbour watermain at the west of the HKCEC.

Indirect impact

Changes in water quality

9.5.3        Potential indirect impacts to the marine habitats and the associated fauna would include changes in water quality due to dredging activities of seabed sediment.


Elevation of suspended solid (SS)

9.5.4        Possible indirect impact on subtidal habitat may include water quality deterioration due to siltation effects during the marine works. Marine fauna especially sessile filter feeders are susceptible to deleterious impacts from sedimentation through smothering and clogging of their respiratory and feeding apparatus. Similarly, more turbid water may reduce the amount of light reaching beneath the water surface, which may also be detrimental to marine flora and fauna. This may result in both direct (e.g. mortality) and indirect (e.g. slow growth rate, low in reproductive success rate) impacts on marine life and may eventually cause the reduction of population size of marine assemblage. Potential secondary impact on the associated avifaunal population foraging within the Victoria Harbour and the CBTS may be resulted due to the reduced food availability caused from the dredging works of this project.

9.5.5        To assess the impacts associated with elevated SS, the assessment was based on compliance with the statutory Water Quality Objectives (WQO) for concerned Water Control Zones, which are set for among other reasons, to offer protection for marine ecological resources. Water quality modelling predictions were analyzed for compliance with the WQO through comparison of worst case scenario’s 15-day depth-averaged SS level against baseline levels.  Using this criterion, if the elevation in SS levels exceeds 30% above ambient baseline conditions, adverse impacts on marine ecology, may be predicted and suitable mitigation pursued.

9.5.6        There are no WQOs regarding sedimentation rates. To assess impacts due to sediment deposition on far-field ecological sensitive receivers, the sedimentation rate of not exceeding 100 mg cm-2 per day (or 0.1 kg m-2 per day) which was also adopted in other EIA studies in Hong Kong for ecological resources conservation (Hyder, 1997; ERM, 2001; Black & Veatch, 2006), is considered as suitable for coral protection in this study.

Release of contaminants and nutrients

9.5.7        As bottom sediment is disturbed during dredging activities and particles released into the water column, organic and inorganic substances contained in the sediment may be released to the water column. Released substances may cause toxic effects to marine fauna.

9.5.8        In addition, the release of inorganic substances may cause eutrophication and algal bloom in the construction area. Oxidation of dead algae may use up some of the oxygen in the water.  If oxygen levels are depleted to low levels, benthic organisms unable to tolerate such conditions may suffer hypoxia-induced mortality and / or stress including reduced feeding and growth rate.  The WQO standard that the average-depth and bottom water DO should remain above 4 mg/L and 2 mg/ L respectively for 90% of the time was adopted.

Disturbance impact

9.5.9        Marine dredging activities and other marine works within the Harbour area may cause disturbance impacts on the associated waterbird population and other avifaunal species of conservation interest due to increase of background noise and marine traffic. 

Operation phase

9.5.10    There is no direct or indirect ecological impact on marine resources expected during the operation phase of this project.


9.6              Evaluation of Ecological Impacts

Construction phase
Direct impact
Habitat loss

9.6.1        Direct impacts to the marine ecological resources would include habitat loss due to the dredging activities in the Assessment Area.  The proposed marine works would lead to the temporary loss of less than 0.5 hectare of soft bottom seabed and subtidal habitats within the coastal area of the Victoria Harbour at the west of the HKCEC. However, the identified feeding ground for waterbirds near the A King Shipyard and the existing natural shoreline at the Kellett Island will remain intact during construction. No direct loss of feeding ground for waterbirds and natural intertidal habitat would be resulted in this Project.

9.6.2        As discussed in Section 9.4, soft bottom seabed and subtidal habitat in the Assessment Area are ranked as very low in ecological importance (very low to low value). No species of conservation interest such as coral was found along the alignment of the new cross harbour watermain. In addition, temporary loss of habitats due to this project would be reinstated after the construction works and similar assemblages of flora and fauna are expected to re-colonise. Therefore, temporary loss of only small areas of these habitats would not result in adverse impact on the marine ecological system in and within the vicinity of the project area.

Indirect impact
Changes in water quality

            Elevation of Suspended Solid (SS)

9.6.3        Dredging activities would temporarily elevate the suspended sediment level and create sediment plumes. Benthic epifauna could be susceptible to the effects of increased sediment loads.  Effects could be lethal or sublethal through reduction in survivalship, growth rate and reproductive potential due to stress incurred by the need to constantly flush out deposited material.  The effects of sedimentation on organisms depend on several factors, such as species tolerance to suspended solids, life modes of organisms (sessile or free-swimming) and water movement. Potential secondary impact of reduced food availability on the associated avifaunal population recorded in the Assessment Area may be resulted if reduction of population size of marine assemblage occurs. However, considering there are a number of similar feeding areas within the Harbour area, the affected bird population is expected to displace to the nearby alternative feeding grounds for foraging and no adverse impact on the associated waterbirds population and other avifaunal species of conservation interest is expected.


9.6.4        Based on the prediction of the construction phase water quality modelling (see water impact assessment), potential water quality impact due to elevation of SS would occur at coastal waters of the Victoria Harbour. It is predicted that impacts to intertidal and subtidal assemblages immediately outside of the dredging sites would occur during the construction phase because the elevation of SS is predicted to be more than 30% increase from ambient level at several locations.  However, implementation of the proposed mitigation measures as suggested in the water quality assessment could effectively minimize this impact to less than 10 mg/L SS elevation in the assessment area. As coral colonies found at the coastlines within ex-PCWA Basin and along seawall at North Point would be translocated to other locations prior to the commencement of construction works of the Scheduled 3 Project, these coral colonies would not be affected by this impact. Considering that the intertidal and subtidal communities identified in the Assessment Area are of generally very low ecological value and in view of the impact of suspended solids elevation is temporary, no adverse indirect ecological impact is anticipated.

9.6.5        Impact is not expected to occur at the far-field ecological sensitive receivers including the coral areas located in the vicinity of Green Island, Little Green Island and Junk Bay.  Sedimentation rate and elevations of SS at these locations are predicted to be less than 0.1 kg m-2 per day and 2 mg L-1 respectively under the worst case scenario.  An elevation of this magnitude is very small and the total SS level is compliant with the WQO criteria for these areas.  Thus, it is expected that adverse impacts to these areas arising from elevated SS levels would not occur.  

9.6.6        The predicted elevation of SS at coastal water of the Kellet Island is less than 10 mg/L under the worst case scenario, implementation of proper mitigation measures could minimise this impact.  In addition, existing man-made vertical seawalls along the shoreline of Kellet Island also provide partial protection to the intertidal fauna assemblage, no adverse impact to the present intertidal community is expected.

            Release of contaminants and nutrients

9.6.7        As the sediment in the Assessment Area is contaminated with heavy metals and organic pollutants, turbulence caused by dredging activities could release these substances to the water column. Increase of toxic substances in water could cause lethal or sublethal effects to subtidal fauna. Degree of toxic level depends on numbers of factors e.g. species tolerance, contaminant levels, water flow rate, etc. An indication of the likelihood of release of contaminants from the marine sediment during dredging is given by the results of the elutriation tests from the laboratory testing conducted under the Phase I and Phase II marine site investigation (SI) works (see water impact assessment, S.5.7.30 – 5.7.48 for details). The elutriate tests indicated that only the levels of silver and mercury measured in two isolated elutriate samples would marginally exceed the WQO standards. Although exceedences were measured in the elutriate samples, it is expected that any release of contaminants during dredging would be quickly diluted by the large volume of marine water within the construction site.  Based on the detected highest concentrations, the required dilution rate to meet the WQO criteria for silver and mercury were calculated to be very low (i.e. 1.5 only), which is expected to be naturally achieved by dynamic water flow within the Harbour area. Meanwhile, the release of contaminants would also be minimised by the use of closed grab dredger and the dispersion of contaminants would be confined within the construction site by silt curtains (Section 5.8).  Thus, it is considered that long-term off-site marine water quality impact would be unlikely and any local water quality impact would be transient. Nevertheless, as subtidal fauna like fish and crab identified in the Assessment Area are mobile, it is likely that they would avoid the dredged area and recolonise after the marine works. Thus, adverse impact due to release of contaminant on subtidal organisms is not expected.

 

 

 

9.6.8        Nutrient level (inorganic nitrogen and phosphorous) may also increase during dredging activities. High levels of nutrients in seawater can cause rapid increases in phytoplankton often to the point where an algal bloom occurs.  An intense bloom of algae can lead to sharp decreases in the levels of DO in the water as dead algae fall through the water column and decompose on the bottom.  Anoxic conditions may result if DO concentration is already low or is not replenished.  This may result in mortality to marine organisms due to oxygen deprivation. Based on the results of water quality modelling (see water quality assessment), it is predicted that the resultant TIN would be slightly higher than the WQO standard (i.e. < 0.4 mg/L) at several locations immediately outside the dredging area, implementation of proper mitigation measures would be adopted to minimise such impact. In contrast, it is predicted that the depth-averaged and bottom minimum DO concentration contours in the Victoria Harbour reveal a similar pattern to that of the baseline condition that the minimum depth-averaged DO is greater than 4.0 mg L-1 (except water around HKCEC which is predicted to be slightly lower than 4.0 mg/L) and the bottom layer minimum DO is greater than
2.0 mg L-1. These results comply with the WQO for DO.

9.6.9        As discussed in Section 9.4, the soft bottom benthic habitats are already highly hypoxic and the associated benthic and subtidal communities in the Assessment Area are of generally very low ecological significance, so adverse impact due to elevation of nutrients level and DO depletion on the associated marine fauna is not expected.

            Disturbance impact

9.6.10    During the marine works, increased marine traffic and noise generated from construction plant and dredging machines could cause disturbance impacts to the associated waterbirds and other avifaunal species of conservation interest foraging in the Harbour area. However, set against the background of intense human activities in Victoria Harbour and the CBTS, the associated avifaunal population are considered already well adapted to human disturbance. It is expected that displacement to the nearby waters for feeding area may occur temporarily but adverse impact is not anticipated.

Overall impact

9.6.11    Based upon the foregoing discussion, no adverse marine ecological impacts associated with the Project are expected to occur during the construction of the Project.  A summary of impact evaluation is presented in Table 9.3.


Table 9.3         Evaluation of Ecological Impacts on Marine Resources during Construction Phase.

Criteria

Construction phase

Habitat loss

Change in water quality

Disturbance impact

Impacted habitat

Benthic and subtidal habitats

Subtidal and intertidal habitats

Feeding ground in CBTS

Habitat quality

Very low to low

Very low to low

Low

Species

No rare species or other species of conservation interest would be affected.

No rare species or other species of conservation interest would be affected.

Little Egret, Great Egret, Black-crowned Night Heron, Black Kite and White-throated Kingfisher would be affected

Size / Abundance

Temporary loss of less than 0.5 ha seabed and subtidal habitat

Large in size

 

Low to moderate species abundance

Low species abundance

Duration

Temporary

Temporary

Temporary

Reversibility

Would recover after construction phase

Would recover after construction phase

Would recover after construction phase

Magnitude

The magnitude of impact is considered as very minor

The magnitude of impact is considered as minor after implementation of proper mitigation measures.

The magnitude of impact is considered as minor.

Ranking of Significance of Impacts

Low

 

Low

 

Low

Overall impact

No adverse impact

 

9.7              Mitigation of Adverse Environmental Impact

 

9.7.1        As no adverse ecological impact on marine habitats and associated wildlife is predicted, no necessary mitigation measure specific for marine ecology is considered as required in this assessment.  The mitigation measures recommended in the water quality impact assessment to control water quality would also serve to protect marine ecological resources from indirect impacts and ensure no adverse impact on marine life would be resulted from this designated project.

9.8              Evaluation of Residual Impacts

 

9.8.1        No residual impact on marine ecology is expected to occur from this project.

9.9              Evaluation of Cumulative Impacts

 

9.9.1        There are several planned or concurrent works for the other projects conducted in and within the vicinity of the Assessment Area, including the following:

·                     Central Reclamation Phase III (CRIII) Project

·                     Hong Kong Convention and Exhibition Centre (HKCEC) Atrium Link Extension Project

·                     Project for the Western Cross Harbour Main from Wan Chai to Tsim Sha Tsui

·                     Western Cross Submarine Gas Pipelines Project

·                     Kai Tak Development (KTD) Project

 

9.9.2        As dredging and filling activities are also included in the above projects, except the HKCEC Project, the most concerned cumulative impact would be the cumulative effect on the deterioration of water quality in the Victoria Harbour.

9.9.3        For all the concurrent projects listed above, water quality modeling (see water quality assessment) predicted that the dredging and reclamation works undertaken for these concurrent projects would result in elevation of SS level of more than 30 % of ambient level at several locations immediately outside the dredged area under the worse case scenario. With the implementation of proper mitigation measure mentioned and recommended in the water quality assessment, cumulative impact on change of water quality in the Assessment Area could be effectively minimized and is expected to be acceptable. Cumulative impact of change of water quality on far-field ecological sensitive receivers including coral areas at Green Island, Little Green Island and Junk Bay is predicted to be complied with the assessment criteria for corals set in this assessment and therefore no adverse cumulative impact on these far-field ecological sensitive receivers is expected to occur.

9.9.4        The other potential cumulative impact would be the cumulative disturbance impact to the marine habitat and the associate wildlife arising from the increased level of human activities and noise from construction and operation phases. Regarding the existing high level of disturbance in the Assessment Area, this cumulative impact  is anticipated to be temporary and minimal. No adverse cumulative impact on the marine habitats and the associated wildlife is expected.

9.10          Environmental Monitoring and Audit

9.10.1         No monitoring programme specific for marine ecology would be required.

9.11          Conclusion

9.11.1    Literature reviews of existing information supplemented with the results of recently undertaken field surveys on marine ecological resources indicated that identified marine habitats within the Assessment Area are of low ecological value.  There are no ecological sensitive receivers, such as SSSIs, Marine Parks and / or Reserves and other areas of ecological importance or conservation interest, in and within the immediate vicinity of the Assessment Area.

9.11.2    Direct and indirect ecological impacts arising from this designated project during construction phase were identified and evaluated. The designated project would result in the temporary loss of less than 0.5 hectare of soft bottom benthic and subtidal habitats in the coastal area of the Victoria Harbour. Considering that the benthic and subtidal habitats within the Assessment Area are of very low ecological value, no adverse direct ecological impact is expected. 

9.11.3         Indirect disturbance impact on the associated waterbirds and other avifaunal species of conservation interest foraging in the Victoria Harbour and the CBTS was expected to occur during the construction phase of this project. Considering the existing background of intense human activities in these areas, the affected wildlife are considered already well adapted to human disturbance and therefore no adverse indirect impact is expected to occur.

9.11.4    Other impacts arsing from this project would be temporary and minimised with implementation of proper mitigation measures. Overall, no adverse ecological impacts on marine resources are anticipated. 


9.12          References

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Thompson, G.B. (2001). Conservation Biology of the Finless Porpoise. Final report submitted to Agriculture and Fisheries Department.

 

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