Figure 1.1- 1.2	Locations of Key Construction Activities in this reporting period
Figure 2.1	Locations of Air and Noise Monitoring Stations and Chek Lap Kok Wind Station
Figure 3.1 Figure 6.1 Figure 6.2 Figure 6.3 Figure 6.4 Figure 6.5	Locations of Water Quality Monitoring Stations Vessel based Dolphin Monitoring Transects in Baseline Monitoring Land based Dolphin Monitoring in Baseline and Construction Phases Sightings Distribution of Chinese White Dolphins Plots of First Sightings of All CWD Groups obtained from Land-based Stations Location for Autonomous Passive Acoustic Monitoring in Baseline and Construction Phases
Figure 7.1	Duration of the SkyPier HSFs travelled through the SCZ for 1 – 31 August 2016

Appendices

Appendix A	Contract Information
Appendix B	Environmental Mitigation Implementation Schedule (EMIS) for Construction Phase
Appendix C	Calibration Certificates
Appendix D	Monitoring Schedule
Appendix E	Monitoring Results
Appendix F	QA/QC Procedure
Appendix G	Status of Environmental Permits and Licences
Appendix H	Cumulative Statistics on Exceedances, Environmental Complaints, Notification of Summons and Status of Prosecutions
Appendix I	Data of SkyPier HSF Movements to/from Zhuhai and Macau (between 1 and 31 August 2016)

Executive summary

The “Expansion of Hong Kong International Airport into a Three-Runway System” (the Project) serves to meet the future air traffic demands at Hong Kong International Airport (HKIA). On 7 November 2014, the Environmental Impact Assessment (EIA) Report (Register No.: AEIAR-185/2014) for the Project was approved and an Environmental Permit (EP) (Permit No.: EP-489/2014) was issued for the construction and operation of the Project.

The land-based construction works of the Contract P560(R) Aviation Fuel Pipeline Diversion Works (Contract P560(R)) commenced on 28 December 2015 on the airport island.

The commencement of initial reclamation works was announced on 1 August 2016. This is the 8^th Construction Phase Monthly EM&A Report for the Project which summarizes the monitoring results and audit findings of the EM&A programme during the reporting period from 1 August 2016 to 31 August 2016.

Key Construction Activities in the Reporting Period

The key construction activities of the Project carried out in the reporting month were related to Contract P560(R) Aviation Fuel Pipeline Diversion Works (Contract P560(R)) which involved drilling a pilot hole using Horizontal Directional Drilling (HDD), stockpiling of excavated materials from HDD operation and site clearance and preparation works at Sheung Sha Chau. The key activities of the four DCM contracts involved mobilization and off-site plant fabrication, and CLP cable diversion enabling work involved site preparation works. Site investigation works were also continued during the reporting period.

EM&A Activities Conducted in the Reporting Period

The monthly EM&A programme was undertaken in accordance with the Updated EM&A Manual of the Project. During the reporting period, the ET conducted thirty-six sets of air quality measurements, twenty-five sets of construction noise measurements, twelve sets of water quality measurements, one ecological monitoring on Sheung Sha Chau Island, two complete sets of small vessel line-transect surveys and five days of land-based theodolite tracking survey effort for Chinese White Dolphin (CWD) monitoring as well as environmental site inspections, landscape & visual and waste monitoring for the Project’s construction works.

On the implementation of the SkyPier Plan, the daily movements of all SkyPier High Speed Ferries (HSFs) in August 2016 were 10 to 94 daily movements, which are within the maximum daily cap of 125 daily movements. A total of 809 HSF movements under SkyPier Plan were recorded. All HSFs had travelled through the SCZ with prevailing speed under 15 knots (5.7 to 14.6 knots) in compliance with the SkyPier Plan. Seven ferry movements had minor deviation from the diverted route. Four of the cases were due to public safety and the remaining three cases are under investigation. In summary, the ET and IEC have audited the HSF movements against the SkyPier Plan and conducted follow up investigation or actions accordingly.

On the implementation of the Marine Travel Routes and Management Plan for Construction and Associated Vessel (MTRMP-CAV), skipper training workshops have been held with concerned captains of construction vessels to familiarise them with the requirements of the Plan. The ET is working with contractors to familiarise with the requirements of the MTRMP-CAV .

Results of Impact Monitoring

Four DCM contracts were awarded in August 2016. The key activity of the four DCM contracts was mobilization and off-site plant fabrication. Water quality monitoring and CWD monitoirng were conducted as scheduled although no marine construction works was carried during the reporting period.

All 1-hour total suspended particulate (TSP), noise and waste were completed in the reporting period for the land-based construction activities. No exceedance of the Action/ Limit Levels was recorded. Monthly ecological monitoring on Sheung Sha Chau Island confirmed that there was no construction works at Sheung Sha Chau and no direct encroachment or disturbance to the identified egretry area.

Summary of Upcoming Key Issues

Major site activities anticipated in the next reporting period for the Project will be under the following contracts including:

Advanced works Contract:

Contract P560 (R) Aviation Fuel Pipeline Diversion Works

● HDD pilot hole drilling;

● Stockpiling of excavated materials from HDD operation; and

● Site clearance and construction work at Sheung Sha Chau.

DCM Contracts:

Contract 3201 to 3204 Deep Cement Mixing Works

● Mobilization;

● Off-site plant fabrication; and

● Site survey and investigation.

Other Contracts:

Contract 3213 CLP Cable Diversion Enabling Works

● Land-based site preparation works.

Site investigation works will continue. The key environmental issues will be associated with dust, noise generation, water quality, construction waste management, CWD, ecological impact on Sheung Sha Chau. The implementation of required mitigation measures by the Contractor will be monitored by the ET.


Land-based CWD Monitoring by Theodolite	Construction Vessel Skipper Training	Skypier Plan Briefing at Integrated Airport Centre

Summary Table

The following table summarizes the key findings of the EM&A programme during the reporting period from 1 to 31 August 2016:

	Yes	No	Details	Analysis / Recommendation / Remedial Actions
Breaches of Limit Level^		ü	No exceedance of project-related limit level was recorded.	Nil
Breaches of Action Level^		ü	No exceedance of project-related action level was recorded.	Nil
Complaints Received		ü	No construction activities related complaints were received.	Nil
Notification of any summons and status of prosecutions		ü	Neither notifications of summons nor prosecution were received.	Nil
Changes that affect the EM&A		ü	There were no changes to the construction works that may affect the EM&A	Nil

Remarks: ^ only exceedance of action/ limit level related to Project works will be highlighted.

1 Introduction

1.1 Background

On 7 November 2014, the Environmental Impact Assessment (EIA) Report (Register No.: AEIAR-185/2014) for the “Expansion of Hong Kong International Airport into a Three-Runway System” (the Project) was approved and an Environmental Permit (EP) (Permit No.: EP-489/2014) was issued for the construction and operation of the Project.

Airport Authority Hong Kong (AAHK) commissioned Mott MacDonald Hong Kong Limited (MMHK) to undertake the role of Environmental Team (ET) for carrying out the Environmental Monitoring & Audit (EM&A) works during the construction phase of the Project in accordance with the Updated EM&A Manual (the Manual) submitted under EP Condition 3.1. The Manual is available on the Project’s dedicated website (accessible at: http://env.threerunwaysystem.com/en/index.html). AECOM Asia Company Limited (AECOM) was employed by AAHK as the Independent Environmental Checker (IEC) for the Project.

The Project covers the expansion of the existing airport into a three-runway system (3RS) with key project components comprising land formation of about 650 ha and all associated facilities and infrastructure including taxiways, aprons, aircraft stands, a passenger concourse, an expanded Terminal 2, all related airside and landside works and associated ancillary and supporting facilities. The existing submarine aviation fuel pipelines and submarine power cables also require diversion as part of the works.

Construction of the Project is to proceed in the general order of diversion of the submarine aviation fuel pipelines, diversion of the submarine power cables, land formation, and construction of infrastructure, followed by construction of superstructures.

The land-based construction works of the Contract P560(R) Aviation Fuel Pipeline Diversion Works (Contract P560(R)) commenced on 28 December 2015 on the airport island.

The commencement of initial reclamation works was announced on 1 August 2016. The updated overall phasing programme of all construction works was presented in Appendix A of the Construction Phase Monthly EM&A Report No. 7. Contracts awarded in August 2016 are presented in Appendix A.

1.2 Scope of this Report

This is the 8^th Construction Phase Monthly EM&A Report for the Project which summarizes the key findings of the EM&A programme during the reporting period from 1 to 31 August 2016.

1.3 Project Organisation

The Project’s organization structure remained unchanged during the reporting month. The Project’s organization structure can be referred to Appendix B of the Construction Phase Monthly EM&A Report No.1. Contact details of the key personnel have been updated and is presented in Table 1.1.

Table 1.1: Contact Information of Key Personnel

Party	Position	Name	Telephone
Project Manager’s Representative (Airport Authority Hong Kong)	Senior Manager, Environment	Lawrence Tsui	2183 2734
Environmental Team (ET) (Mott MacDonald Hong Kong Limited)	Environmental Team Leader	Terence Kong	2828 5919
	Deputy Environmental Team Leader	Heidi Yu	2828 5704
	Deputy Environmental Team Leader	Keith Chau	2972 1721
Independent Environmental Checker (IEC) (AECOM Asia Company Limited)	Independent Environmental Checker	Jackel Law	3922 9376
	Deputy Independent Environmental Checker	Joanne Tsoi	3922 9423
Advanced Works Contract:
Contract P560(R) Aviation Fuel Pipeline Diversion Works (Langfang Huayuan Mechanical and Electrical Engineering Co., Ltd.)	Project Manager	Shih Wei	2117 0566
	Environmental Coordinator	Ivy Tam	2151 2090
DCM Works Contracts:
Contract 3201 DCM (Package 1) (Penta-Ocean-China State-Dong-Ah Joint Venture)	Project Director	Mr. Tsugunari SUZUKI	9178 9689
	Environmental Officer	Mr. Kanny CHO	9019 1962
Contract 3202 DCM (Package 2) (Samsung-BuildKing Joint Venture)	Project Manager	Mr. Ilkwon Nam	9643 3117
	Environmental Officer	Mr. Dickson Mak	9525 8408
Contract 3203 DCM (Package 3) (Sambo E&C Co.,Ltd)	Deputy Project Manager	Mr. Park Seong Jae	9683 8693
	Environmental Officer	Mr. Leung Min Pong	9203 5820
Contract 3204 DCM (Package 4) (CRBC-SAMBO Joint Venture)	Project Manager	Mr. Allan Tam	9703 0256
	Environmental Officer	Mr. David Man	6421 3238
Other Works contract:
Contract 3213 CLP Cable Diversion Enabling Works (Wing Hing Construction Company)	Project Manager	Mr. Wyman Lau	6112 9753

1.4 Summary of Construction Works

During the reporting period, no construction work was carried out by DCM works contracts and CLP cable diversion enabling works contract. Key construction activities of the Project were related to the Contract P560(R) Aviation Fuel Pipeline Diversion Works (Contract P560(R)) which involved drilling of HDD pilot hole at the HDD launching site located at the west part of the airport and site clearance and preparation works at Sheung Sha Chau.

The excavated materials from HDD operation were stockpiled at the stockpile area located near Chun Ming Road adjacent to Tradeport Logistic Centre on the airport island.

The HDD launching site and stockpiling area are around 3 km and 900m away respectively from the nearest air and noise sensitive receivers in Tung Chung and the villages in North Lantau. The locations of the works areas are presented in Figure 1.1 to Figure 1.2. Some site investigation works were carried out during the reporting period.

1.5 Summary of EM&A Programme Requirements

As presented in the Updated EM&A Manual, the environmental aspects of interest for the Project include air quality, noise, water quality, waste management, land contamination, terrestrial ecology, marine ecology, fisheries, landscape & visual, sewage and sewerage, and hazard to human life.

The status for all environmental aspects is presented Table 1.2. The EM&A requirements remained unchanged during the reporting period and details can be referred to Table 1.2 of the Construction Phase Monthly EM&A Report No. 1.

Table 1.2: Summary of status for all environmental aspects under the Updated EM&A Manual

Parameters	Status
Air Quality
Baseline Monitoring	The baseline air quality monitoring result has been reported in Baseline Monitoring Report (Version 1) and submitted to EPD on 14 December 2015 under EP Condition 3.4.
Impact Monitoring	On-going
Noise
Baseline Monitoring	The baseline noise monitoring result has been reported in Baseline Monitoring Report (Version 1) and submitted to EPD on 14 December 2015 under EP Condition 3.4.
Impact Monitoring	On-going
Water Quality
General Baseline Water Quality Monitoring for reclamation, water jetting and field joint works	The baseline water quality monitoring result has been reported in Water Quality Baseline Monitoring Report and submitted to EPD under EP Condition 3.4.
General Impact Water Quality Monitoring for reclamation, water jetting and field joint works	The general water quality monitoring commenced on 4 August 2016 as scheduled, although there were no marine construction works.
Initial Intensive Deep Cement Mixing (DCM) Water Quality Monitoring	To be commenced according to the detailed plan on DCM
Early/ Regular DCM Water Quality Monitoring	The early regular DCM water quality monitoring commenced on 4 August 2016 as scheduled, although there were no marine construction works.
Waste Management
Waste Monitoring	On-going
Land Contamination
Supplementary Contamination Assessment Plan (CAP)	To be submitted with the relevant construction works
Contamination Assessment Report (CAR) for Golf Course	The CAR for Golf Course was submitted to EPD on 17 March 2016. EPD had no adverse comment on the CAR for Golf Course on 6 April 2016.
Terrestrial Ecology
Pre-construction Egretry Survey Egretry Survey Plan	The revised Egretry Survey Plan was submitted and approved by EPD on 25 April 2016 under EP Condition 2.14.
Ecological Monitoring	On-going
Marine Ecology
Pre-Construction Phase Coral Dive Survey	The Coral Translocation Plan was approved by EPD on 6 June 2016 under EP Condition 2.12.
Chinese White Dolphins (CWD)
Vessel survey, land-based theodolite track and passive acoustic monitoring (PAM)
Baseline Monitoring	Baseline CWD results were reported in the CWD Baseline Monitoring Report as submitted to EPD on 15 July 2016 in accordance with EP Condition 3.4. The CWD Baseline Monitoring Report was approved by EPD on 25 July 2016.
Impact Monitoring	Monitoring of CWDs commenced in August 2016 as schedueled , although there were no marine construction works.
Landscape & Visual
Baseline Monitoring	The baseline landscape & visual monitoring result has been reported in Baseline Monitoring Report (Version 1) and submitted to EPD on 14 December 2015 under EP Condition 3.4.
Impact Monitoring	On-going
Environmental Auditing
Regular site inspection	On-going
SkyPier High Speed Ferries (HSF) implementation measures	On-going
Construction and Associated Vessels Implementation measures	On-going
Complaint Hotline and Email channel	On-going
Environmental Log Book	On-going

Taking into account the construction works in this reporting month, impact monitoring of air quality, noise, waste management, ecology and landscape & visual were carried out in the reporting month. No marine construction works was conducted during the reporting period. Water quality monitoring and CWD monitoring were conducted as scheduled although there were no marine construction works during the reporting period. The EM&A programme also involved weekly site inspections and related auditings conducted by the ET for checking the implementation of the required environmental mitigation measures recommended in the approved EIA Report.

The EM&A programme has been following the recommendations presented in the approved EIA Report and the Updated EM&A Manual. A summary of implementation status of the environmental mitigation measures for the construction phase of the Project during the reporting period is provided in Appendix B.

2 Air Quality Monitoring

2.1 Monitoring Stations

Air quality monitoring was conducted at two representative monitoring stations in the vicinity of air sensitive receivers in Tung Chung and villages in North Lantau in accordance with the Updated EM&A Manual. Table 2.1 describes the details of the monitoring stations. Figure 2.1 shows the locations of the monitoring stations.

Table 2.1: Locations of Impact Air Quality Monitoring Stations

Monitoring Station	Location
AR1A	Man Tung Road Park
AR2	Village House at Tin Sum

2.2 Monitoring Requirements and Schedule

In accordance with the Updated EM&A Manual, baseline 1-hour total suspended particulate (TSP) levels at the two air quality monitoring stations were established as presented in the Baseline Monitoring Report (Version 1 dated December 2015). Impact 1-hour TSP monitoring was conducted for three times every 6 days. The Action and Limit Levels of the air quality monitoring are provided in Table 2.2.

The scheduled impact 1-hour TSP monitoring at AR1A on 2 August 2016 was cancelled due to adverse weather. The monitoring at AR1A on 2 August 2016 was rescheduled to 3 August 2016.

The air quality monitoring schedule involved in the reporting period is provided in Appendix D.

Table 2.2: Action and Limit Levels for 1-hour TSP

Monitoring Station	Action Level (mg/m³)	Limit Level (mg/m³)
AR1A	306	500
AR2	298	500

2.3 Monitoring Equipment

Portable direct reading dust meter was used to carry out the 1-hour TSP monitoring. The brand and model of the equipment are given in Table 2.3.

Table 2.3: Air Quality Monitoring Equipment

Equipment	Brand and Model
Portable direct reading dust meter (Laser dust monitor)	SIBTA LD-3B-002 (Serial No. 974350)

2.4 Monitoring Methodology

2.4.1 Measuring Procedure

The measurement procedures involved in the impact 1-hr TSP monitoring can be summarised as follows:

a. The portable direct reading dust meter was mounted on a tripod at a height of 1.2 m above the ground.

b. Prior to the measurement, the equipment was set up for 1 minute span check and 6 second background check.

c. The one hour dust measurement was started. Site conditions and dust sources at the nearby area were recorded on a record sheet.

d. When the measurement completed, the “Count” reading per hour was recorded for result calculation.

2.4.2 Maintenance and Calibration

The portable direct reading dust meter is calibrated every year against high volume sampler (HVS) to check the validity and accuracy of the results measured by direct reading method. The calibration certificates of the portable direct reading dust meter are provided in Appendix C. The corresponding calibration record of the HVS is also given in Appendix C.

2.5 Analysis and Interpretation of Monitoring Results

The monitoring results for 1-hour TSP are summarized in Table 2.4. Detailed impact monitoring results are presented in Appendix E.

Table 2.4: Summary of 1-hour TSP Monitoring Results

Monitoring Station	1-hr TSP Concentration Range (mg/m³)	Action Level (mg/m³)	Limit Level (mg/m³)
AR1A	20 - 150	306	500
AR2	17 - 90	298	500

No exceedance of the Action /Limit Level was recorded at all monitoring stations in the reporting period.

General meteorological conditions throughout the impact monitoring period were recorded. Wind data for each monitoring day including wind speed and wind direction was collected from the Chek Lap Kok Wind Station.

3 Noise Monitoring

3.1 Monitoring Stations

Noise monitoring was conducted at five representative monitoring stations in the vicinity of noise sensitive receivers in Tung Chung and villages in North Lantau in accordance with the Updated EM&A Manual. Figure 2.1 shows the locations of the monitoring stations and these are described in Table 3.1 below. As described in Section 4.3.3 of the Updated EM&A Manual, monitoring at NM2 will commence when the future residential buildings in Tung Chung West Development become occupied.

Table 3.1: Locations of Impact Noise Monitoring Stations

Monitoring Station	Location	Type of measurement
NM1A	Man Tung Road Park	Free field
NM2⁽¹⁾	Tung Chung West Development	To be determined
NM3A	Site Office	Facade
NM4	Ching Chung Hau Po Woon Primary School	Free field
NM5	Village House in Tin Sum	Free field
NM6	House No. 1, Sha Lo Wan	Free field

Note: (1) As described in Section 4.3.3 of the Updated EM&A Manual, noise monitoring at NM2 will only commence after occupation of the future Tung Chung West Development.

3.2 Monitoring Requirements and Schedule

In accordance with the Updated EM&A Manual, baseline noise levels at the noise monitoring stations were established as presented in the Baseline Monitoring Report (Version 1 dated December 2015). Impact noise monitoring was conducted once per week in the form of 30-minute measurements of L_eq, L₁₀ and L₉₀ levels recorded at each monitoring station between 0700 and 1900 on normal weekdays. The Action and Limit levels of the noise monitoring are provided in Table 3.2. The construction noise monitoring schedule involved in the reporting period is provided in Appendix D.

Table 3.2: Action and Limit Levels for Construction Noise

Monitoring Stations

Time Period

Action Level

Limit Level, L_eq(30mins) dB(A)

NM1A, NM2, NM3A, NM4, NM5 and NM6

0700-1900 hours on normal weekdays

When one documented

complaint is received from

any one of the sensitive

receivers

75 dB(A)⁽ⁱ⁾

Note: ⁽ⁱ⁾ reduce to 70dB(A) for school and 65dB(A) during school examination periods.

3.3 Monitoring Equipment

Noise monitoring was performed using sound level meter at each designated monitoring station. The sound level meters deployed comply with the International Electrotechnical Commission Publications 651:1979 (Type 1) and 804:1985 (Type 1) specifications. Acoustic calibrator was used to check the sound level meters by a known sound pressure level for field measurement. The brand and model of the equipment are given in Table 3.3.

Table 3.3: Noise Monitoring Equipment

Equipment

Brand and Model

Integrated Sound Level Meter

B&K 2238 (Serial No. 2800932)

B&K 2238 (Serial No. 2684503)

B&K 2238 (Serial No. 2381580)

B&K 2238 (Serial No. 2808432)

Acoustic Calibrator

B&K 4231 (Serial No. 3003246)

B&K 4231 (Serial No. 3004068)

3.4 Monitoring Methodology

3.4.1 Monitoring Procedure

The monitoring procedures involved in the noise impact monitoring can be summarised as follows:

a. The sound level meter was set on a tripod at least a height of 1.2 m above the ground for free-field measurements at monitoring stations NM1A, NM4, NM5 and NM6. A correction of +3 dB(A) was applied to the free field measurements.

b. Façade measurements were made at the monitoring station NM3A.

c. Parameters such as frequency weighting, time weighting and measurement time were set.

d. Prior to and after each noise measurement, the meter was calibrated using the acoustic calibrator. If the difference in the calibration level before and after measurement was more than 1 dB(A), the measurement would be considered invalid and repeat of noise measurement would be required after re-calibration or repair of the equipment.

e. During the monitoring period, L_eq, L₁₀ and L₉₀ were recorded. In addition, site conditions and noise sources were recorded on a record sheet.

f. Noise measurement results were corrected with reference to the baseline monitoring levels.

g. Observations were recorded when high intrusive noise (e.g. dog barking, helicopter noise) was observed during the monitoring.

3.4.2 Maintenance and Calibration

The maintenance and calibration procedures are summarised below:

a. The microphone head of the sound level meter was cleaned with soft cloth at regular intervals.

b. The meter and calibrator were sent to the supplier or laboratory accredited under Hong Kong Laboratory Accreditation Scheme (HOKLAS) to check and calibrate at yearly intervals.

Calibration certificates of the sound level meters and acoustic calibrators used in the noise monitoring are provided in Appendix C.

3.5 Analysis and Interpretation of Monitoring Results

The construction noise monitoring results are summarized in Table 3.4 and the detailed monitoring data are provided in Appendix E.

Table 3.4: Summary of Construction Noise Monitoring Results

Monitoring Station	Noise Level Range, dB(A) L_{eq (30 mins)}	Limit Level, dB(A) L_{eq (30 mins)}
NM1A⁽ⁱ⁾	68 - 72	75
NM3A	60 - 63	75
NM4⁽ⁱ⁾	63 - 65	70⁽ⁱⁱ⁾
NM5⁽ⁱ⁾	53 - 59	75
NM6⁽ⁱ⁾	67 - 71	75

Note: (i) +3 dB(A) Façade correction included;

(ii) Reduced to 65 dB(A) during school examination periods.

As the construction activities were far away from the monitoring stations, major sources of noise dominating the monitoring stations observed during the construction noise impact monitoring were aircraft noise at NM3A and NM5, aircraft noise and helicopter noise at NM6, road traffic noise at NM1A and school activities at NM4 in this reporting month.

No exceedance of the Action/ Limit Level was recorded at all monitoring stations in the reporting period.

4 Water Quality Monitoring

4.1 Monitoring Stations

Water quality monitoring was conducted at a total of 22 water quality monitoring stations, comprising 12 impact stations, seven sensitive receiver stations and three control stations in the vicinity of water quality sensitive receivers around the airport island in accordance with the Updated EM&A Manual. Table 4.1 describes the details of the monitoring stations. Figure 3.1 shows the locations of the monitoring stations.

Table 4.1: Monitoring Locations and Parameters for Impact Water Quality Monitoring

Monitoring Stations		Coordinates
Monitoring Stations	Description	Easting	Northing	Parameters
C1	Control	804247	815620
C2	Control	806945	825682
C3	Control	817803	822109
IM1	Impact	806458	818351	DO, pH, Temperature, Salinity, Turbidity, SS, Total Alkalinity, Heavy Metals⁽²⁾
IM2	Impact	806193	818852
IM3	Impact	806019	819411
IM4	Impact	805039	819570
IM5	Impact	804924	820564
IM6	Impact	805828	821060
IM7	Impact	806835	821349
IM8	Impact	807838	821695
IM9	Impact	808811	822094
IM10	Impact	809838	822240
IM11	Impact	810545	821501
IM12	Impact	811519	821162
SR1⁽¹⁾	Future Hong Kong-Zhuhai-Macao Bridge Hong Kong Boundary Crossing Facilities (HKBCF) Seawater Intake for cooling	812586	820069	DO, pH, Temperature, Salinity, Turbidity, SS
SR2	Planned marine park / hard corals at The Brothers / Tai Mo To	814166	821463
SR3	Sha Chau and Lung Kwu Chau Marine Park / fishing and spawning grounds in North Lantau	807571	822147
SR4A	Sha Lo Wan	807810	817189
SR5A	San Tau Beach SSSI	810696	816593
SR6	Tai Ho Bay, Near Tai Ho Stream SSSI	814663	817899
SR7	Ma Wan Fish Culture Zone (FCZ)	823742	823636
SR8	Seawater Intake for cooling at Hong Kong International Airport (East)	811593	820417

Notes:

⁽¹⁾ the seawater intakes of SR1 for the future HKBCF is not yet in operation, the future permanent location for SR1

during impact monitoring is subject to finalisation after the HKBCF seawater is commissioned.

⁽²⁾ According to the Baseline Water Quality Monitoring Report, Chromium and Nickel are the representative heavy metals for early regular DCM monitoring. DCM specific water quality monitoring parameters (total alkalinity and heavy metals) were only conducted at C1 to C3, IM1 to IM12 .

4.2 Monitoring Requirements and Schedule

In accordance with the Updated EM&A Manual, baseline water quality levels at the abovementioned representative water quality monitoring stations were established as presented in the Baseline Water Quality Monitoring Report.

General and early regular DCM water quality monitoring was conducted three days per week, at mid-flood and mid-ebb tides, at the 22 water quality monitoring stations during the reporting period, although there were no marine construction works. The sea condition varied from clam to rough, and the weather varied from fine to rainy during the monitoring period.

The scheduled water quality monitoring on 2 August 2016 during ebb and flood tides and 18 August 2016 during ebb tide were cancelled due to adverse weather. The water quality monitoring schedule for the reporting period is provided in Appendix D.

4.2.1 Action and Limit Levels for Water Quality Monitoring

The Action and Limit Levels levels for general water quality monitoring and regular DCM monitoring are presented in Table 4.2. The control and impact stations during flood tide and ebb tide for general water quality monitoring and regular DCM monitoring are presented in Table 4.3.

Table 4.2: Action and Limit Levels for general water quality monitoring and regular DCM monitoring

Parameters	Action Level (AL)		Limit Level (LL)
Action and Limit Levels for general water quality monitoring and regular DCM monitoring (excluding SR1& SR8)
DO in mg/L (Surface, Middle & Bottom)	Surface and Middle 4.8 mg/L		Surface and Middle 4.1 mg/L 5 mg/L for Fish Culture Zone (SR7) only
DO in mg/L (Surface, Middle & Bottom)	Bottom 3.1 mg/L		Bottom 2.3 mg/L
Suspended Solids (SS) in mg/L	25	or 120% of upstream control station at the same tide of the same day, whichever is higher	36	or 130% of upstream control station at the same tide of the same day, whichever is higher
Turbidity in NTU	26.0		41.4
Total Alkalinity in ppm	95		98
Representative Heavy Metals for early regular DCM monitoring (Chromium)	0.2		0.2
Representative Heavy Metals for early regular DCM monitoring (Nickel)	3.2		3.4
Action and Limit Levels SR1
SS (mg/l)	To be determined prior to its commissioning		To be determined prior to its commissioning
Action and Limit Levels SR8
SS (mg/l)	52		60

Note:

1. For DO measurement, non-compliance occurs when monitoring result is lower than the limits.

2. For parameters other than DO, non-compliance of water quality results when monitoring results is higher than the limits.

3. Depth-averaged results are used unless specified otherwise.

4. Details of selection criteria for the two heavy metals for early regular DCM monitoring refer to the Detailed Plan on Deep Cement Mixing available on the dedicated 3RS website http://env.threerunwaysystem.com/en/ep-submissions.html)

5. The action and limit levels for the two representative heavy metals chosen will be the same as that for the intensive DCM monitoring.

Table 4.3: The Control and Impact stations during flood tide and ebb tide for general water quality monitoring and regular DCM monitoring

Control Station	Impact Stations
Flood Tide
C1	IM1, IM2, IM3, IM4, IM5, IM6, IM7, IM8, SR3
SR2^{^1}	IM7, IM8, IM9, IM10, IM11, IM12, SR1A, SR3, SR4A, SR5A, SR6, SR8
Ebb Tide
C1	SR4A, SR5A, SR6
C2	IM1, IM2, IM3, IM4, IM5, IM6, IM7, IM8, IM9, IM10, IM11, IM12, SR1A, SR2, SR3, SR7, SR8

^{^1}As per findings of Baseline Water Quality Report, the control reference will be changed from C3 to SR2 from 1 Sep 2016 onwards.

4.3 Monitoring Equipment

Table 4.4 summarises the equipment used in the impact water quality monitoring programme.

Table 4.4: Water Quality Monitoring Equipment

Equipment	Brand and Model
Water Sampler	Van Dorn Water Sampler
Positioning Device (measurement of GPS)	Garmin eTrex Vista HCx
Water Depth Detector (measurement of water depth)	Lowrance Mark 5x
Multifunctional Meter (measurement of DO, pH, temperature, salinity and turbidity)	YSI 6920 V2 (serial no. 000109DF and 00019CB2)
Current Meter (measurement of current speed and direction)	Sontek HydroSurveyor
Digital Titrator (measurement of total alkalinity)	Titrette Digital Burette 50ml Class A (serial no.10N64701 and 10N60623)

4.4 Monitoring Methodology

4.4.1 Measuring Procedure

Water quality monitoring samples were taken at three depths (at 1m below surface, at mid-depth, and at 1m above bottom) for locations with water depth >6m. For locations with water depth between 3m and 6m, water samples were taken at two depths (surface and bottom). For locations with water depth <3m, only the surface depth was taken. Duplicate water samples were taken and analysed.

The water samples for all monitoring parameters were collected, stored, preserved and analysis according to the Standard Methods, APHA 22^nd ed. and/or other methods as agreed by the EPD. In-situ measurements at monitoring locations including temperature, pH, DO, turbidity, salinity and water depth were collected by equipment listed in the following. Water samples for heavy metals and SS analysis were stored in high density polythene bottles with no preservative added, packed in ice (cooled to 4 ºC without being frozen), delivered to the laboratory within 24 hours of collection.

4.4.2 Maintenance and Calibration

Calibration of In-situ instruments

All in-situ monitoring instrument were checked, calibrated and certified by a laboratory accredited under HOKLAS before use. Responses of sensors and electrodes were checked with certified standard solutions before each use.

Wet bulb calibration for a DO meter was carried out before commencement of monitoring and after completion of all measurements each day. Calibration was not conducted at each monitoring location as daily calibration is adequate for the type of DO meter employed. A zero check in distilled water was performed with the turbidity probe at least once per monitoring day. The probe should then be calibrated with a solution of known NTU. In addition, the turbidity probe was calibrated at least twice per month to establish the relationship between turbidity readings (in NTU) and levels of suspended solids (in mg/L). Accuracy check of the digital titrator was performed at least once per monitoring day.

Calibration certificates of the monitoring equipment used in the monitoring are provided in Appendix D.

4.4.3 Laboratory Measurement / Analysis

Analysis of SS and heavy metals have been carried out by a HOKLAS accredited laboratory, ALS Technichem (HK) Pty Ltd (Reg. No. HOKLAS 066). Sufficient water samples were collected at all the monitoring stations for carrying out the laboratory SS and heavy metals determination. The SS and heavy metals determination works were started within 24 hours after collection of the water samples. The analysis of SS and heavy metals have followed the standard methods summarised in Table 4.5. The QA/QC procedures for laboratory measurement/ analysis of SS and heavy metals were followed and presented in Appendix F.

Table 4.5: Laboratory measurement/ analysis of SS and heavy metals

Parameters	Instrumentation	Analytical Method	Reporting Limit
Suspended Solid (SS)	Analytical Balance	APHA 2540D	2 mg/L
Heavy Metals
Chromium (Cr)	ICP-MS	USEPA 6020A	0.2 µg/L
Nickel (Ni)	ICP-MS	USEPA 6020A	0.2 µg/L

4.5 Analysis and Interpretation of Monitoring Results

The commencement of initial reclamation works was announced on 1 August 2016. Four DCM contracts were awarded in August 2016. The key activity of the four marine DCM contracts was only mobilization and off-site plant fabrication. No marine construction works was conducted during the reporting period.

The general water quality monitoring was completed as scheduled and the results showed that some parameter such as DO was appeared to reflect the seasonal low of surrounding water body according to EPD’s long-term marine water quality monitoring data. As the water quality monitoring results were collected before the commencement of marine construction works, the measurement data collected in August 2016 may take into account for reviewing the baseline water quality condition.

Water quality monitoring results and graphical presentations are provided in Appendix E.

5 Waste Management

5.1 Monitoring Requirements

In accordance with the Updated EM&A Manual, the waste generated from construction activities was audited once per week to determine if wastes are being managed in accordance with the Waste Management Plan (WMP) prepared for the Project, contract-specific WMP, and any statutory and contractual requirements. All aspects of waste management including waste generation, storage, transportation and disposal were assessed during the audits. The Action and Limit levels of the construction waste are provided in Table 5.1.

Table 5.1: Action and Limit Levels for Construction Waste

Monitoring Stations

Action Level

Limit Level

Construction Area

When one valid documented complaint is

received

Non-compliance of the WMP, contract-specific

WMPs, any statutory and contractual

requirements

5.2 Waste Management Status

No construction work for four DCM contracts and CLP cable diversion enabling works was undertaken and hence no waste was generated during the reporting period.

Weekly monitoring of Contract P560(R) Aviation Fuel Pipeline Diversion Works was carried out by the ET on 3, 10, 17, 24 and 31 August 2016 to check and monitor the implementation of proper waste management practices during the construction phase.

For Contract P560(R) Aviation Fuel Pipeline Diversion Works, recommendations were provided during monitoring including provision of drip tray for the oil drums on 24 August 2016, removal of oil stain on ground as chemical waste on 17, 24 and 31 August 2016. The contractor had followed up with implementation of mitigation measures.

The P560(R) Contractor was advised to properly maintain a recording system, maximize the reuse of C&D materials and properly maintain site tidiness.

Based on the updated information, about 210 m³ excavated materials were produced from the HDD launching site in August 2016. The generated excavated materials were temporarily stored at storage and stockpiling area at Chun Ming Road adjacent to Tradeport Logistic Centre on the airport island. The excavated material will be reused in the Project.

In addition, metals, paper and plastic were recycled during the reporting month. 3.9 tonnes of general refuse were disposed of to the West New Territories (WENT) Landfill and 0.16 tonnes of chemical waste was disposed of to the Tsing Yi Chemical Waste Treatment Centre in August 2016. No Construction and Demolition (C&D) material was disposed off-site during the reporting month.

No exceedances of the Action and Limit Levels were recorded in the reporting period.

6 Chinese White Dolphin Monitoring

6.1 CWD Monitoring Requirements

In accordance with the Updated EM&A Manual, CWD monitoring by small vessel line-transect survey supplemented by land-based theodolite tracking should be conducted during construction phase. The monitoring was completed in the reporting period, although there were no marine construction works.

The small vessel line-transect survey as proposed in the Updated EM&A Manual should be conducted at a frequency of two full survey per month while land-based theodolite tracking should be conducted at a frequency of one day per month per station during the construction phase. In addition to the land-based theodolite tracking required for impact monitoring as stipulated in the EM&A Manual, some supplemental theodolite tracking have also been taken during the initial implementation period for the SkyPier HSF diversion and speed control in order to assist in monitoring the effectiveness of these measures, i.e. in total twice per month at the Sha Chau station and three times per month at the Lung Kwu Chau station.

The Action Level (AL) and Limit Level (LL) for CWD monitoring were formulated by the action response approach using the running quarterly dolphin encounter rates STG and ANI derived from baseline monitoring data, as presented in the CWD Baseline Monitoring Report. The derived values of AL and LL for CWD monitoring were summarized in Table 6.1.

Table 6.1: Derived Values of Action Level (AL) and Limit Level (LL) for Chinese White Dolphin Monitoring

	NEL, NWL, AW, WL and SWL as a Whole
Action Level	Running quarterly* STG < 1.86 & ANI < 9.35
Limit Level	Two consecutive running quarterly^ (3-month) STG < 1.86 & ANI < 9.35

[Notes for Table 6.1 (referring to the baseline monitoring report):

*Action Level – running quarterly STG & ANI would be calculated from the three preceding survey months, e.g. works commenced on 1 August 2016,this CWD impact monitoring report reviewed the data from 18 May to 17 June 2016 covering two sets of transect surveys for all monitoring areas, and the data collected in July and August 2016 (also with two sets of transect surveys for all monitoring areas) for calculating the quarterly encounter rates STG & ANI. For CWD impact monitoring for September 2016, data from 1 July to 30 September 2016 will be used to calculate the quarterly encounter rates STG & ANI;

^Limit Level – two consecutive running quarters mean since works commenced on 1 August 2016, the first running quarter for reporting will be 18 May to 17 June 2016, July 2016 to August 2016, and the second running quarter will be July 2016 to September 2016.

AL and/or LL will be exceeded if both STG and ANI fall below the criteria.]

6.2 CWD Monitoring Transects and Stations

6.2.1 Small Vessel Line-transect Survey

Small vessel line-transect surveys were conduct along the transects covering Northeast Lantau (NEL), Northwest Lantau (NWL), Airport West (AW), West Lantau (WL) and Southwest Lantau (SWL), as proposed in the Updated EM&A Manual and being consistent with the AFCD long-term monitoring programme (except AW). The AW transect has not been previously surveyed in the AFCD programme due to the restrictions of HKIA Exclusion Zone, nevertheless, this transect was established during the EIA of the 3RS project with the aim to collect project specific baseline information within the HKIA Approach Area to fill the data gap that was not covered by the AFCD programme. This provided a larger sample size for estimating the densities and patterns of movements in the broader study area of the project.

For the NWL area, there was no physical demarcation of the 3RS works area yet during CWD monitoring survey in the reporting period, therefore the works area of the 3RS project was still accessible and the transect lines followed the waypoints and lengths conducted for baseline monitoring. These transect lines were depicted in Figure 6.1 while the coordinates of all transect lines are shown in Table 6.2.

Table 6.2: Coordinates of Transect Lines in NEL, NWL, AW, WL and SWL Survey Areas

Waypoint	Easting	Northing	Waypoint	Easting	Northing
NEL
1S	813525	820900	6N	818568	824433
1N	813525	824657	7S	819532	821420
2S	814556	818449	7N	819532	824209
2N	814559	824768	8S	820451	822125
3S	815542	818807	8N	820451	823671
3N	815542	824882	9S	821504	822371
4S	816506	819480	9N	821504	823761
4N	816506	824859	10S	822513	823268
5S	817537	820220	10N	822513	824321
5N	817537	824613	11S	823477	823402
6S	818568	820735	11N	823477	824613
NWL
1S	804671	814577	5N	808504	828602
1N	804671	831404	6S	809490	820590
2S	805475	815457	6N	809490	825352
2N	805476	830562	7S	810499	820950
3S	806464	819550	7N	810499	824613
3N	806464	829598	8S	811508	821250
4S	807518	819900	8N	811508	824254
4N	807518	829230	9S	812516	821250
5S	808504	820250	9N	812516	824254
AW
1W	804730	818220	2W	805051	817156
1E	806519	818271	2E	806913	817076
WL
1W	800600	805450	7W	800400	811450
1E	801760	805450	7E	802400	811450
2W	800300	806450	8W	800800	812450
2E	801750	806450	8E	802900	812450
3W	799600	807450	9W	801500	813550
3E	801500	807450	9E	803120	813550
4W	799400	808450	10W	801880	814500
4E	801430	808450	10E	803700	814500
5W	799500	809450	11W	802860	815500
5E	801300	809450	12S/11E	803750	815500
6W	799800	810450	12N	803750	818500
6E	801400	810450
SWL
1S	802494	803961	6S	807467	801137
1N	802494	806174	6N	807467	808458
2S	803489	803280	7S	808553	800329
2N	803489	806720	7N	808553	807377
3S	804484	802509	8S	809547	800338
3N	804484	807048	8N	809547	807396
4S	805478	802105	9S	810542	800423
4N	805478	807556	9N	810542	807462
5S	806473	801250	10S	811446	801335
5N	806473	808458	10N	811446	809436

6.2.2 Land-based Theodolite Tracking

Land-based theodolite tracking stations were set up at two locations, one facing east/south/west on the southern slopes of Sha Chau (SC), and the other facing north/northeast/northwest at Lung Kwu Chau. The stations (D and E) are depicted in Figure 6.2 and shown in Table 6.3 with position coordinates, height of station and approximate distance of consistent theodolite tracking capabilities for CWD.

Table 6.3: Land-based Survey Station Details

Stations

Location

Geographical Coordinates

Station Height (m)

Approximate Tracking Distance (km)

Sha Chau (SC)

22° 20’ 43.5” N

113° 53’ 24.66” E

45.66

Lung Kwu Chau (LKC)

22° 22’ 44.83” N

113° 53’ 0.2” E

70.40

6.3 CWD Monitoring Methodology

6.3.1 Small Vessel Line-transect Survey

Small vessel line-transect surveys provided data for density and abundance estimation and other assessments using distance-sampling methodologies, specifically, line-transect methods.

The surveys involved small vessel line-transect data collection and have been designed to be similar to, and consistent with, previous surveys for the Agriculture, Fisheries and Conservation Department (AFCD) for their long-term monitoring of small cetaceans in Hong Kong. The survey was designed to provide systematic, quantitative measurements of density, abundance and habitat use.

As mentioned in Section 6.2.1, the transects covered Northeast Lantau (NEL), Northwest Lantau (NWL) covering the Airport West (AW), West Lantau (WL) and Southwest Lantau (SWL) as proposed in the Updated EM&A Manual and are consistent with the AFCD long-term monitoring programme (except AW). There are two types of transect lines:

● Primary transect lines: the parallel and zigzag transect lines as shown in Figure 6.1; and

● Secondary transect lines: transect lines connecting between the primary transect lines and crossing islands.

All on-effort data collected under conditions of Beaufort 0-3 and visibility of approximately 1200 m or beyond, on both primary and secondary transect lines, were used for analysis.

A 15-20 m vessel with a flying bridge observation platform about 4 to 5 m above water level and unobstructed forward view, and a team of three to four observers were deployed to undertake the surveys. Two observers were on search effort at all times when following the transect lines with a constant speed of 7 to 8 knots (i.e. 13 to 15 km per hour), one using 7X handheld binoculars and the other using unaided eyes and recording data.

During on-effort survey periods, the survey team recorded effort data including time, position (waypoints), weather conditions (Beaufort sea state and visibility) and distance travelled in each series with assistance of a handheld GPS device. The GPS device also continuously and automatically logged data including time, position (Latitude and longitude) and vessel speed throughout the entire survey.

When CWDs were seen, the survey team was taken off-effort, the dolphins were approached and photographed for photo-ID information (using a Canon 7D [or similar] camera and long 300 mm+ telephoto lens), then followed until they left the study area or were lost. At that point, the boat returned (off effort) to the next survey line and began to survey on effort again.

Focal follows of dolphins were conducted where practicable (i.e. when individual dolphins or small stable groups of dolphins with at least one member that could be readily identifiable with unaided eyes during observations and weather conditions are favourable). These involved the boat following (at an appropriate distance to minimize disturbance) an identifiable individual dolphin for an extended period of time, and collecting detailed data on its location, behaviour, response to vessels, and associates.

6.3.2 Photo Identification

Chinese White Dolphins can be identified by their unique features like presence of scratches, nick marks, cuts, wounds, deformities of their dorsal fin and distinguished colouration and spotting patterns.

When CWDs were observed, the survey team was taken off-effort, the dolphins were approached and photographed for photo-ID information (using a Canon 7D [or similar] camera and long 300 mm+ telephoto lens). The survey team attempted to photo both sides of every single dolphin in the group as the colouration and spotting pattern on both sides may not be identical. The photos were taken at the highest available resolution and stored on Compact Flash memory cards for transferring into a computer.

All photos taken were initially examined to sort out those containing potentially identifiable individuals. These sorted-out images would then be examined in detail and compared to the CWD photo-identification catalogue established for 3RS during the baseline monitoring stage.

6.3.3 Land-based Theodolite Tracking

Land-based monitoring obtains fine-scale information on the time of day and movement patterns of the CWDs. A digital theodolite (Sokkia/Sokkisha Model DT5 or similar equipment) with 30-power magnification and 5-s precision was used to obtain the vertical and horizontal angle of each dolphin and vessel position. Angles were converted to geographic coordinates (latitude and longitude) and data were recorded using Pythagoras software, Version 1.2. This method delivers precise positions of multiple spatially distant targets in a short amount of time. The technique is fully non-invasive, and allows for time and cost-effective descriptions of dolphin habitat use patterns at all times of daylight.

Three surveyors (one theodolite operator, one computer operator, and one observer) were involved in each survey. Observers searched for dolphins using unaided eyes and handheld binoculars (7X50). Theodolite tracking sessions were initiated whenever an individual CWD or group of CWDs was located. Where possible, a distinguishable individual was selected, based on colouration, within the group. The focal individual was then continuously tracked via the theodolite, with a position recorded each time the dolphin surfaced. In case an individual could not be positively distinguished from other members, the group was tracked by recording positions based on a central point within the group whenever the CWD surfaced. Tracking continued until animals were lost from view, moved beyond the range of reliable visibility (>1-3 km, depending on station height), or environmental conditions obstructed visibility (e.g., intense haze, Beaufort sea state >4, or sunset), at which time the research effort was terminated. In addition to the tracking of CWD, all vessels that moved within 2-3 km of the station were tracked, with effort made to obtain at least two positions for each vessel.

Theodolite tracking included focal follows of CWD groups and vessels. Priority was given to tracking individual or groups of CWD. The survey team also attempted to track all vessels moving within 1 km of the focal CWD.

6.4 Monitoring Results and Observations

6.4.1 Small Vessel Line-transect Survey

Survey Effort

Within the monitoring month of August 2016, two complete sets of small vessel line-transect surveys were conducted on the 5^th , 9^th 10^th, 15^th, 19^th, 22^nd, 24^th and 25^th August 2016, covering all transects in NEL, NWL, AW, WL and SWL survey area for twice.

A total of 469.08 km of survey effort was collected from these surveys, with 91.8% of the total survey effort being conducted under favourable weather condition (i.e. Beaufort Sea State 3 or below with favourable visibility). Details of the survey effort may refer to Appendix E.

Sighting Distribution

In August 2016, 19 groups of CWD with 69 individuals were sighted. Amongst the sightings of CWD, 15 groups with 61 individuals were made during on-effort search under favourable weather condition (i.e. Beaufort Sea State 3 or below with favourable visibility). For details of cetacean sightings refer to Appendix E.

Distribution of CWD sightings recorded in August 2016 is illustrated in Figure 6.3. The sightings were mainly located east of Lung Kwu Chau and in Urmston Road near Castle Peak Power Station in the NWL survey area, and Tai O, Yi O and Peaked Hill in the WL survey area. No sightings of CWDs were recorded within or in close proximity to the 3RS land-formation footprint.

Figure 6.3: Sightings Distribution of Chinese White Dolphins

[Pink circle: Sighting locations of CWD, White line: Vessel survey transects, Blue polygon: Sha Chau and Lung Kwu Chau Marine Park (SCLKCMP), Red polygon: 3RS land-formation footprint]

Note: Only on-effort sightings under Beaufort 3 or below were presented in the figure.

Encounter Rate

Two types of dolphin encounter rates were calculated based on the data from August 2016. They included the number of dolphin sightings per 100km survey effort (STG) and total number of dolphins per 100km survey effort (ANI) in the whole survey area (i.e. NEL, NWL, AW, WL and SWL). In the calculation of dolphin encounter rates, only survey data collected under favourable weather condition (i.e. Beaufort Sea State 3 or below with favourable visibility) were used. Formulations of the encounter rates are shown as below:

Encounter Rate of Number of Dolphin Sightings (STG)

Encounter Rate of Number of Dolphins (ANI)

(Notes: Only data collected under Beaufort 3 or below condition was used)

In August 2016, a total of 430.61 km of survey effort was collected under Beaufort Sea State 3 or below with favourable visibility, whilst total no. of 15 on-effort sightings and total number of 61 dolphins from on-effort sightings were collected under such condition. Calculation of the encounter rates in August 2016 are shown as below:

Encounter Rate of Number of Dolphin Sightings (STG) in August 2016

Encounter Rate of Number of Dolphins (ANI) in August 2016

For the reporting month, in the running quarter a total of 1195.86 km of survey effort was collected under Beaufort Sea State 3 or below with favourable visibility, whilst total no. of 59 on-effort sightings and total number of 246 dolphins from on-effort sightings were collected under such condition. Calculation of the running quarterly encounter rates are shown as below:

Running Quarterly Encounter Rate of Number of Dolphin Sightings (STG)

Running Quarterly Encounter Rate of Number of Dolphins (ANI)

The STG and ANI of CWD in the whole survey area (i.e. NEL, NWL, AW, WL and SWL) of August 2016 and the running quarterly STG and ANI calculated from the three preceding survey months are presented in Table 6.4 below.

Table 6.4: STG and ANI of Chinese White Dolphin of the Whole Survey Area in August 2016 and Running Quarterly STG and ANI

	Encounter Rate (STG)	Encounter Rate (ANI)
August 2016	3.48	14.17
Running Quarterly*	4.93	20.57

*Running quarterly encounter rates STG & ANI for reporting were calculated from the three preceding survey months, i.e. the data from 18 May to 17 June 2016, the data in July 2016 and August 2016, containing six sets of transect surveys for all monitoring areas.

Group Size

In August 2016, the average group size of CWDs was 4.1 individuals per group. The majority of the CWD groups were medium in size with 3-9 individuals. Five groups out of 15 were small in size with 1-2 individuals. No large CWD groups with 10 or more individuals were sighted in August 2016.

Activities and Association with Fishing Boats

No CWDs were sighted with association with operating fishing boats in August 2016.

Mother-calf Pair

Three pairs of mother-and-calf and mother-and-spotted juvenile (SJ) pairs were sighted. Two pairs were sighted in the WL survey area while the remaining pair was sighted in the NWL survey area.

6.4.2 Photo Identification

In August 2016, a total number of 22 different CWD individuals were identified. Amongst these 22 identified individuals, seven (NLMM028, NLMM035, NLMM036, NLMM037, NLMM038, SLMM011 and SLMM015) were sighted for twice and one (NLMM002) was sighted three times in August. A summary of photo identification works is presented in Table 6.5. Representative photos of these individuals may refer to Appendix E.

Table 6.5: Summary of Photo Identification in August 2016

Individual ID	No. of times sighted	Date of sighting (yyyymmdd)	Individual ID	No. of times sighted	Date of sighting (yyyymmdd)
WLMM030	1	20160809	WLMM043	1	20160809
WLMM046	1	20160809	NLMM002	3	20160819, 20160824
NLMM035	2	20160819	NLMM036	2	20160819
NLMM037	2	20160819	NLMM004	1	20160819
NLMM028	2	20160822, 20160824	NLMM038	2	20160822, 20160824
WLMM038	1	20160822	WLMM047	1	20160822
WLMM048	1	20160822	WLMM049	1	20160822
NLMM005	1	20160822	NLMM019	1	20160822
SLMM015	2	20160822	SLMM010	1	20160822
SLMM011	2	20160822, 20160825	NLMM006	1	20160824
NLMM010	1	20160824	NLMM013	1	20160824

6.4.3 Land-based Theodolite Tracking

Survey Effort

Land-based theodolite tracking surveys at Lung Kwu Chau were conducted on 5^th, 11^th and 23^rd August 2016 and at Sha Chau on 1^st and 9^th August 2016. A total of 5 days of land-based theodolite tracking survey effort have been accomplished in August 2016. A total number of 12 CWD groups were tracked during the surveys. Information of survey effort and CWD groups sighted during these land-based theodolite tracking surveys are presented in Table 6.6. Details of the survey effort and CWD groups tracked are presented in Appendix E. The first sighting locations of CWD groups tracked during land-based theodolite tracking surveys in August 2016 were depicted in Figure 6.4.

Table 6.6: Summary of Survey Effort and CWD Group of Land-based Theodolite Tracking

Land-based Station	# of Survey Sessions	Survey Effort (hh:mm)	# CWD Groups Sighted	CWD Group Sighting per Survey Hour
Lung Kwu Chau	3	18:11	11	0.607
Sha Chau	2	12:10	1	0.083
TOTAL	5	30:21	12	0.395

Figure 6.4: Plots of First Sightings of All CWD Groups obtained from Land-based Stations

[Green triangle: LKC station; Green square: CWD group off LKC; Yellow triangle: SC station; Yellow square: CWD group off SC; Blue line: SCLKCMP boundary; Red line: 3RS land-formation footprint]

6.5 Progress Update on Passive Acoustic Monitoring

Underwater acoustic monitoring using Passive Acoustic Monitoring (PAM) should also be undertaken within the whole duration for land formation related construction works. An Ecological Acoustic Recorder (EAR) has been deployed and positioned at south of Sha Chau Island with 20% duty cycle (Figure 6.5). The PAM deployment is generally last for4-6 weeks prior to data retrieval as one batch of data for analysis. Acoustic data will be gathered to listen for CWDs occurrence patterns and to obtain anthropogenic noise information simultaneously. Analysis (by a specialized team of acousticians) involved manually browsing through every acoustic recording and logging the occurrence of dolphin signals. All data will be re-played by computer and listened to by human ears for accurate assessment of dolphin group presence. As the period of data collection and analysis takes more than two months, PAM results could not be reported in monthly intervals.

The EAR was deployed on 15 August 2016 in this reporting period and scheduled to be retrieved on 12 September 2016. Data transfer and analysis of this batch of PAM data are tentatively scheduled for completion by end of November 2016.

6.6 Site Audit for CWD-related Mitigation Measures

There were no marine construction activities underway in the reporting month. Contract-specific Marine Mammal Watching Plan and Dolphin Exclusion Zone Plan were still under preparation by contractors in this time-period, therefore audits of acoustic decoupling and dolphin exclusion zone implementation were not applicable during this reporting period.

Audits of SkyPier High Speed Ferries route diversion and speed control and construction vessel management are presented in Section 7.2 and Section 7.3 respectively.

6.7 Timing of Reporting CWD Monitoring Results

For indication, detailed analysis of CWD monitoring results collected by small vessel line-transect survey (such as distribution of group size, activities/boat association, mother-calf pairs and re-sightings) will be provided in future quarterly reports. Detailed analysis of CWD monitoring results collected by land-based theodolite tracking (such as time of day or year, group size, behavioural state and vessel activity) and PAM will be provided in future yearly reports when a larger sample size of data be collected for supplementing the findings from vessel based monitoring.

6.8 Summary of CWD Monitoring

No marine construction works was conducted during the reporting period. CWD monitoring was conducted as scheduled although no marine construction works was carried out during the reporting period. The baseline conditions for the CWD will be reviewed and the Event and Action Plan will be further reviewed when 12-month CWD data be collected.

7 Environmental Site Inspection and Audit

7.1 Environmental Site Inspection

No construction work for four DCM contracts and CLP cable diversion enabling works was undertaken during the reporting period, thus no weekly site inspection for those contracts was conducted during the reporting period.

Weekly site inspection of the construction works for P560(R) was carried out by the ET on 3, 10, 17, 24 and 31 August 2016 to monitor the implementation of proper environmental pollution control and mitigation measures for the Project. Site inspections were also conducted independently by the Project’s Independent Environmental Checker (IEC) on 5 and 17 August 2016. Observations have been recorded in the site inspection checklists and passed to the Contractor together with the appropriate recommended mitigation measures where necessary.

The key observations from site inspection and associated recommendations were related to the improvement of efficiency of sedimentation tank, provision of drip tray for chemical containers, proper maintenance of drip tray, and removal of oil stains on ground as chemical waste.

A summary of implementation status of the environmental mitigation measures for the construction phase of the Project during the reporting period is provided in Appendix B.

7.2 Audit of Route Diversion and Speed Control of the SkyPier High Speed Ferries

The Marine Travel Routes and Management Plan for High Speed Ferries of SkyPier (the SkyPier Plan) has been submitted to the Advisory Council on the Environment (ACE) for comment and subsequently submitted to and approved by EPD in November 2015 under EP Condition 2.10. The approved SkyPier Plan is available on the dedicated website of the Project. In the SkyPier Plan, AAHK committed to implementing the mitigation measure of requiring high speed ferries (HSFs) of SkyPier travelling between HKIA and Zhuhai / Macau to start diverting the route with an associated speed control across an area (i.e. Speed Control Zone (SCZ)) with high Chinese White Dolphin (CWD) abundance. The route diversion and speed restriction at the SCZ have been implemented since 28 December 2015.

Key audit findings for the SkyPier HSFs travelling to/from Zhuhai and Macau against the requirements of the SkyPier Plan during the reporting period are summarized in Table 7.1. The daily movements of all SkyPier HSFs in August 2016 were within the maximum daily cap number (i.e. 10 to 94 daily movements, which are within maximum daily cap of 125 daily movements). There are fewer ferry movements on 1^st and 2^nd August 2016 (52 and 10 movements respectively ) due to Typhoon. Status of compliance with annual daily average of 99 movements will be further reviewed in the annual EM&A Report.

In total, 809 ferry movements between HKIA SkyPier and Zhuhai / Macau were recorded in August 2016 and the data are presented in Appendix I. The time spent for the SkyPier HSFs travelled through the SCZ in August were presented in Figure 7‑1. It will take 9.6 minutes to travel through the SCZ when the SkyPier HSFs adopt the maximum allowed speed of 15-knot within the SCZ. Figure 7‑1 shows that all the SkyPier HSFs spent more than 9.6 minutes to travel through the SCZ.

Figure 7‑1 Duration of the SkyPier HSFs travelled through the SCZ for 1 – 31 August 2016

Seven ferry movements were recorded with minor deviation of diverted route on 3, 4, 14, 15, 18, 26 and 28 August 2016. Notices were sent to the ferry operators and the investigation results revealed that they were related to safety / emergency situations presented as follows:

● Cases on 3 and 15 August 2016: HSF captains reported that they had to give way to other vessels for safety reason and were not able to enter the SCZ through the gate access points. Then the HSF returned to the normal route following the SkyPier Plan.

● Case on 4 and 18 August 2016: HSF captains reported that the deviation was due to strong tidal wave and current.

● Case on 14, 26 and 28 August 2016: These cases are under investigation.

Cases of minor route deviation in July 2016 have been followed up. For the cases on 1, 8, 9, 11, 12 and 15 July 2016, similar minor deviations of diverted route were observed. The six cases were recorded with the same ferry. Repeated deviations were recorded with the same captain for the five cases on 8, 9, 11, 12 and 15 July 2016 and another captain is responsible for the remaining case on 1 July 2016. The ferry operator reported that the deviations were due to strong tidal wave and current and wrong reference points of SCZ were applied. The instantaneous speeds of all the above cases were within the 15-knot speed limit. Warning letter has been issued to the concerned ferry operator to prevent reoccurrence. The ferry operator is also recommended to check the coordinates of SCZ plotted on the radar. Refresher training to the two concerned vessel captains will be provided by experienced captain of the concerned ferry operator to ensure the captains are familiarised with the SkyPier Plan requirements.

For the case on 22 July 2016, investigation found that the vessel captain was required to give way to other vessels for safety reason. After that, the HSF returned to the normal route following the SkyPier Plan.

Table 7.1: Summary of Key Audit Findings against the SkyPier Plan

Requirements in the SkyPier Plan	1 August to 31 August 2016
Total number of ferry movements recorded and audited	809
Use diverted route and enter / leave SCZ through Gate Access Points	7 deviations (FO were requested to provide further supporting evidence for investigation)
Speed control in speed control zone	All HSFs were within 15 knots (5.7 knots to 14.6 knots), which complied with the SkyPier Plan. The time used by HSF to travel through SCZ is presented in Figure 7‑1.
Daily Cap (including all SkyPier HSFs)	10 to 94 daily movements (within maximum daily cap - 125 daily movements) There are fewer ferry movements on 1^st and 2^nd August 2016 (52 and 10 movements respectively ) due to Typhoon.

7.3 Audit of Construction and Associated Vessels

The Marine Travel Routes and Management Plan for Construction and Associated Vessel (MTRMP-CAV) has been submitted and approved in December 2015 by EPD under EP Condition 2.9. The approved Plan is available on the dedicated website of the Project.

Although no major construction activities were conducted in August 2016, skipper training workshops have been held with concerned captains of construction vessels associated with Contract P560(R) Aviation Fuel Pipeline Diversion Works and the four DCM contracts to familiarise them with the predefined routes, general education on local cetaceans, guidelines for avoiding adverse water quality impact, the required environmental practices / measures while operating construction and associated vessels under the Project, and guidelines for operating vessels safely in the presence of CWDs.

The ET will work with new Contractors mobilising for 3RS works on reviewing and helping them familiarise with the requirements of the MTRMP-CAV.

ET has audited of all the relevant information, including AIS data, vessel tracks, record of potential deviations and the responses provided by concerned captain, to ensure full compliance with the requirements of the MTRMP-CAV. Weekly audits have been conducted in August to ensure that sufficient information has been provided by Marine Traffic Control Center (MTCC). The IEC of the Project has also performed audit on the compliance of the requirements as part of the EM&A programme.

7.4 Ecological Monitoring

In accordance with the Updated EM&A Manual, ecological monitoring shall be undertaken monthly at the HDD daylighting location on Sheung Sha Chau Island to identify and evaluate any impacts with appropriate actions taken as required to address and minimise any adverse impact found. Monthly ecological monitoring on Sheung Sha Chau Island observed one suspected late breeding/nursery activitiy of egret at the southern side of the island and confirmed that there was no construction works at Sheung Sha Chau and thus no direct encroachment or disturbance to the identified egretry area.

7.5 Status of Submissions under Environmental Permits

The current status of submissions under the EP up to the reporting period is presented in Table 7.2.

Table 7.2: Status of Submissions under Environmental Permit

EP Condition	Submission	Status
2.1	Complaint Management Plan	Accepted / approved by EPD
2.4	Management Organizations
2.5	Construction Works Schedule and Location Plans
2.7	Marine Park Proposal
2.8	Marine Ecology Conservation Plan
2.9	Marine Travel Routes and Management Plan for Construction and Associated Vessels
2.10	Marine Travel Routes and Management Plan for High Speed Ferries of SkyPier
2.11	Marine Mammal Watching Plan
2.12	Coral Translocation Plan
2.13	Fisheries Management Plan
2.14	Egretry Survey Plan
2.15	Silt Curtain Deployment Plan
2.17	Detailed Plan on Deep Cement Mixing
2.16	Spill Response Plan
2.19	Waste Management Plan
3.1	Updated EM&A Manual
3.4	Baseline Monitoring Report

7.6 Compliance with Other Statutory Environmental Requirements

During the reporting period, environmental related licenses and permits required for the construction activities were checked. No non-compliance with environmental statutory requirements was recorded. The environmental licenses and permits which are valid in the reporting month are presented in Appendix G.

7.7 Analysis and Interpretation of Complaints, Notification of Summons and Status of Prosecutions

7.7.1 Complaints

During the reporting period, no construction activities related complaints were received.

7.7.2 Notifications of Summons or Status of Prosecution

During the reporting period, neither notifications of summons nor prosecution were received.

7.7.3 Cumulative Statistics

Cumulative statistics on complaints, notifications of summons and status of prosecutions are summarized in Appendix H.

8 Future Key Issues and Other EIA & EM&A Issues

8.1 Construction Programme for the Coming Reporting Period

Major site activities anticipated in the next reporting period for the Project will be under the following contracts including:

Advance works Contract:

Contract P560 (R) Aviation Fuel Pipeline Diversion Works

● HDD pilot hole drilling;

● Stockpiling of excavated materials from HDD operation; and

● Site clearance and construction work at Sheung Sha Chau.

DCM Contracts:

Contract 3201 to 3204 Deep Cement Mixing Works

● Mobilization;

● Off-site plant fabrication; and

● Site survey and investigation.

Other Contracts:

Contract 3213 CLP Cable Diversion Enabling Works

● Land-based site preparation works.

Site investigation works will continue to carry out to support design process.

8.2 Key Environmental Issues for the Coming Reporting Period

The key environmental issues for the Project in the coming reporting period are expected to be associated with the construction activities include:

● Generation of dust from construction works;

● Noise impact from operating equipment and machinery on-site;

● Generation of site surface runoffs and wastewater from activities on-site;

● Management of stockpiles;

● Sorting, recycling, storage and disposal of general refuse and construction waste;

● Management of chemicals and avoidance of oil spillage on-site; and

● Acoustic decoupling measures for equipment on marine vessel.

The implementation of required mitigation measures by the Contractor will be monitored by the ET.

8.3 Monitoring Schedule for the Coming Reporting Period

A tentative schedule of the planned environmental monitoring work in the next reporting period is provided in Appendix D.

9 Conclusion and Recommendation

The key construction activities of the Project carried out in the reporting month were related to Contract P560(R) which involved drilling of HDD pilot hole, stockpiling of excavated materials from HDD operation and site clearance and preparation works at Sheung Sha Chau. Works under the other four DCM contracts involved mobilization and off-site plant fabrication, and CLP cable diversion enabling work involved site preparation works. Some site investigation works were also carried out during the reporting period.

Construction dust, noise, waste and ecological monitoring were carried out in the reporting period.

As observed on site and confirmed by the contractor, no marine construction works was conducted during the reporting period. The water quality monitoring and CWD monitoring were completed as scheduled although no marine construction works was carried out during the reporting period.

No breach of the Action or Limit Levels in relation to the air quality, construction noise, waste and ecological monitoring were recorded in the reporting month. All site observations made by the ET were recorded in the site inspection checklists and passed to the Contractor together with the recommended follow-up actions.

On the implementation of the SkyPier Plan, the daily movements of all SkyPier HSFs in August 2016 were 10 to 94 daily movements, which are within the maximum daily cap of 125 daily movements. A total of 809 HSF movements under SkyPier Plan were recorded in August 2016. All HSFs had travelled through the SCZ with prevailing speed under 15 knots (5.7 to 14.6 knots) in compliance with the SkyPier Plan. Seven ferry movements showed minor deviations from the diverted route. Four of the cases were due to public safety and the remaining three cases are under investigation. In summary, the ET and IEC have audited the HSF movements against the SkyPier Plan and conducted follow up investigation or actions accordingly.