13                                        Environmental Monitoring & Audit Measures

13.1                                  Introduction

The assessments presented in the preceding sections have predicted that the implementation of the Project is not expected to give rise to any adverse environmental impacts.  A focused EM&A programme is considered appropriate, however, to ensure that the proposed mitigation measures are effectively implemented and the quality of the surrounding environment is not prejudiced.  This section presents the scope of the EM&A requirements.

An EM&A programme will only be required for the construction and post-construction phases of this Project.  Unacceptable environmental impacts are not predicted to occur during the operation of the Project, thus specific operation phase EM&A measures are not considered necessary.  A summary of the requirements for each of the environmental parameters is detailed in Table 13.1.

Table 13.1      Summary of EM&A Requirements

Parameter

Phases

Construction Phase

Post – Construction Phase

Operation Phase

Air Quality

M (a) + SI

-

-

Noise

M (a) + SI

-

-

Water Quality

M (a) + SI (b)

-

-

Waste

SI (b)

-

-

Terrestrial Ecology

SI (b)

-

M

Fisheries

-

-

-

Landscape and Visual

SI (b)

SI (b)

-

Land Contamination

-

-

-

Cultural Heritage

(c)

-

-

Notes:

(a)        M – Environmental monitoring for River Modification and Associated Works

(b)        SI -  Site inspection for both River Modification and Associated Works and Advanced Works

(c)        The project proponent should inform AMO immediately in case of discovery of antiquities or supposed antiquities in the course of excavation works. No monitoring or site inspection is required for archaeology & built heritage.  

13.2                                  EM&A Manual and Implementation Schedule

A detailed EM&A Manual has been prepared for this Project as part of the EIA study.  The following sections provide a summary of the need for monitoring and auditing of the individual environmental aspects.

In accordance with the requirements of the EIA Study Brief, an Implementation Schedule of the environmental mitigation measures recommended in the EIA study has been prepared in form of a checklist.  The Implementation Schedule is presented in Annex H and also attached to the EM&A Manual.

13.3                                  Air Quality

Dust monitoring is recommended during the River Modification Works to ensure compliance with the Total Suspended Particulate (TSP) criterion at the representative Air Sensitive Receivers (ASRs).  Dust monitoring should be undertaken at the air monitoring station at Ta Kwu Ling Village (AM1) and Tsung Yuen Ha (AM2) during construction in works areas III are IV and works areas I are II, respectively (see Figure 13.1).  Regular site audits at the frequency of once a month should be conducted for both the Advanced Works and River Modification contracts to ensure that the recommended mitigation measures are properly implemented during the construction stage. 

13.4                                  Noise

Noise monitoring is recommended during the River Modification Works to ensure compliance with the noise criterion at the representative Noise Sensitive Receivers (NSRs).  Weekly noise monitoring should be undertaken at the noise monitoring station at Ta Kwu Ling Village (NM1) and Kaw Liu Tsuen (NM2) (see Figure 13.1) during construction in works areas III and IV.  Regular site audits at the frequency of once a month should be conducted for both the Advanced Works and River Modification contracts to ensure that the recommended mitigation measures are properly implemented during the construction stage. 

13.5                                  Water Quality

With proper implementation of the recommended mitigation measures, sediment dispersion is not expected to cause adverse water quality impacts at the identified water sensitive receivers.  However, a monitoring programme is recommended to verify the predictions of the EIA and ensure compliance with the assessment criteria.

Based on the construction methodology, the sediment will be excavated in dry within cofferdam.  Water quality monitoring is thus recommended during the foundation pit drainage and cofferdam demolition activities where there is a potential for the release of suspended solids (SS) at the following locations:

During foundation pit drainage and cofferdam demolition at Work Area I and Work Area II

·           500 m upstream of Work Area I; and

·           1,000 m downstream of Work Area II.

During foundation pit drainage and cofferdam demolition at Work Area III and Work Area IV

·           500 m upstream of Work Area III; and

·           1,000 m downstream of Work Area IV.

There will be one monitoring station at each location (ie a total of four monitoring stations).  Monitoring will be conducted for three times per week during the construction period.  The interval between two sampling surveys will not be less than 36 hours.  During each sampling survey, water samples for laboratory analysis and in situ measurements will be taken at all monitoring stations for the following water quality parameters:

·           Dissolved Oxygen (mg L-1) (in situ);

·           pH (in situ);

·           Turbidity (NTU) (in situ); and

·           Suspended Solids (mg L-1) (laboratory analysis).

Monthly site inspections and audits will be conducted to ensure that the recommended mitigation measures are properly implemented during the construction stage. 

13.5.2                            Operation Phase

Adverse water quality impact is not expected during operation phase and hence monitoring is not considered necessary.  In fact the water quality will be monitored through the existing monitoring programme along Shenzhen River.

13.6                                  Terrestrial Ecology

No ecological mitigation measures apart from the adoption of good construction practise are required as part of the environmental monitoring and audit procedures during the construction phase.  The list of good construction practice is provided in Annex H.

The implementation of the landscape works adopting ecological design at Hong Kong side will be checked as part of the environmental monitoring and audit procedures after the completion of construction. 

Although no adverse residual impacts are envisaged based on the results of impact assessment, wetland dependent bird monitoring for one year is recommended after the establishment of the landscape plantings of the Project.  The purpose of the operation monitoring is to review the performance of the reprovisioned/reinstated habitats.  Particular focus will be made on bird species of conservation interest (especially ardeid species including Chinese Pond Heron, Black-crowned Night Heron, Grey Heron, Great Egret, Intermediate Egret and Little Egret, and two wetland dependant species Common Teal and White-breasted Waterhen).

Standard, quantitative point count surveys will be undertaken at designated sampling locations at once per month after the establishment of the landscape plantings of the Project.  The necessity for further ecological monitoring would be reviewed after the first year ecological monitoring programme.  Locations of sampling transects shall include reprovisioned/reinstated habitats including riverbank landscape areas, floodplains and watercourse, and other reference locations within Hong Kong boundary.  Details of the monitoring programme will be formulated and further submitted under the Project.

13.7                                  Fisheries

No impacts to pond fish culture are expected as a result of the construction and operation of the Project.  Therefore, no fisheries-specific mitigation measures are required.  The development and implementation of a monitoring and audit programme designed to assess the effects of the activities on pond culture fish resources is also not deemed necessary.

13.8                                  Land Contamination

Based on the findings of a desktop review and the site investigation for the Project, no further investigation is warranted and no mitigation measures are required during the construction and operation of the Project.

As no potential risks to receptors anticipated, no environmental monitoring and audit programme is deemed necessary. 

13.9                                  Waste Management

A Waste Management Plan (WMP), which will form part of the Environmental Management Plan (EMP) in accordance with ETWB TC(W) No. 19/2005, incorporates mitigation measures that have been proposed in the EIA Report to avoid or reduce potential adverse environmental impacts associated with handling, collection and disposal of waste arising from the construction and operation of this Project.  The WMP shall be prepared and implemented in accordance with ETWB TC(W) No. 19/2005.  Proposed measures are recommended based on good management, control and practices of a construction site.

In order to confirm that the contractor has implemented the recommendations of the EIA Report, monthly site inspections and audits will be conducted of the waste streams, to determine if wastes are being managed in accordance with the approved procedures and the site Waste Management Plan during the construction phase.  The inspections/audits will look at all aspects of waste management including waste generation, storage, recycling, transport and disposal. 

13.10                              Cultural Heritage

The archaeological survey identified only the secondary archaeological deposits at Chuk Yuen and Pak Fu Shan sections (i.e. Sections 2 and 4) of the Project.  The chance of finding in situ archaeological deposits is very low.  Thus no impact on significant archaeological resources is anticipated and no archaeological monitoring is required.  Other sections (i.e. Sections 1, 3 and 5) have been identified with no archaeological potential where no impact is anticipated.  Thus no archaeological monitoring is required.  Pursuant to the Antiquities and Monuments Ordinance, the project proponent should inform the AMO immediately in case of discovery of antiquities or supposed antiquities in the course of soil excavation works in construction stage.

However, it should be noted that the archaeological impact assessment covered only the works area assigned as at the date of this report.  If the works boundary changes in later stage to cover additional area not covered in the EIA, the need for further archaeological survey and subsequent impact assessment should be reviewed and AMO should be consulted.

As no direct or indirect impacts on the identified built heritage sites are anticipated due to their large separation distance from the Project Site, no mitigation measures are considered necessary.  As such, no built heritage monitoring and audit is required. 

13.11                              Landscape & Visual

The Landscape and Visual Impact Assessment of the EIA recommended a series of mitigation measures to mitigate the landscape and visual impacts of the Project.  Implementation of the mitigation measures for landscape and visual resources recommended by the EIA will be monitored through the site inspection and audit programme.

The completed landscape works adopting ecological design on the Hong Kong side will be monitored during the one year establishment period.