Drainage Services Department

 

Agreement No. CE 66/2001(EP)

 

EIA and TIA Studies for the Stage 2 of PWP Item No. 215DS -
Yuen Long and Kam Tin Sewerage and Sewage Disposal (YLKTSSD)

 

Environmental Impact Assessment (Final)

 

Sections 15 to 20

 

Mar 2004

 

 

Ove Arup & Partners Hong Kong Ltd

In association with Archeological Assessment, Ecosystems and Urbis

Level 5, Festival Walk, 80 Tat Chee Avenue, Kowloon Tong, Kowloon, Hong Kong

Tel +852 2528 3031  Fax +852 2268 3950

www.arup.com

 

Job number

23527


CONTENTS[Comment1] 

 

Sections 1 to 5

Sections 6 to 9

Sections 10 to 11

Sections 12 to 14

 

15.0         Cultual Heritage assessment  169

15.1         Legislation and Standards169

15.2         Existing/Baseline Condition169

15.3         Assessment Methodology for Construction Phase181

15.4         Results of the desk-based Study182

15.5         Results of Built Heritage Survey (Construction Phase)185

15.6         Results of the Archaeological Field Evaluation (Construction Phase)189

15.7         Assessment Results for Built Heritage (Construction Phase)192

15.8         Assessment Results on Archaeology (Construction Phase)198

15.9         Mitigation Measures on Built Heritage for Construction Phase199

15.10       Mitigation Measures on Archaeology for Construction Phase205

15.11       Assessment Methodology for Operational Phase205

15.12       Assessment Results for Operational Phase206

15.13       Mitigation Measures for Operational Phase208

16.0         Fishery impact  211

16.1         Legislation and Standards211

16.2         Assessment Methodology211

16.3         Fisheries Baseline Condition212

16.4         Impact Identification and Evaluation for Construction Phase213

16.5         Impact Avoidance and Mitigation Measures for Construction Phase215

16.6         Impact Identification and Evaluation for Operational Phase216

16.7         Impact Avoidance and Mitigation Measures for Operational Phase216

17.0         Environmental Monitoring and Audit (EM&A)219

17.1         Air Quality Impact219

17.2         Noise Impact219

17.3         Water Quality Assessment220

17.4         Waste Management220

17.5         Land Contamination Implications221

17.6         Ecological Assessment221

17.7         Landscape and Visual Impacts221

17.8         Cultural Heritage Assessment221

17.9         Fisheries Assessment224

18.0         Summary of Environmental Outcomes  225

18.1         Air Quality Impact225

18.2         Noise Impact225

18.3         Water Quality Impact225

18.4         Waste Management Implications226

18.5         Land Contamination Impact226

18.6         Ecological Impact227

18.7         Landscape and Visual Impact228

18.8         Cultural Heritage Impact229

18.9         Fisheries Impact231

18.10       Summary of Options Review  231

19.0         CONCLUSION  233

19.1         Air Quality233

19.2         Noise233

19.3         Water Quality Assessment234

19.4         Waste Management235

19.5         Land Contamination Assessment235

19.6         Ecological Assessment235

19.7         Landscape & Visual Impact Assessment236

19.8         Archaeology Assessment236

19.9         Built Heritage Assessment237

19.10       Fisheries Assessment238

20.0         references  239

 

Key to Figures and Appendices

 


15.0      Cultual Heritage assessment

15.1      Legislation and Standards

The following two Ordinances are the main tools for the protection of Cultural Heritage in Hong Kong:

 

15.1.1   Antiquities and Monuments Ordinance

The Antiquities and Monuments Ordinance (Cap. 53) was enacted in 1976 and provides the statutory framework to provide for the preservation of objects of historical, archaeological and palaeontological interest.

 

The Ordinance contains the statutory procedures for the Declaration of Monuments. The proposed monument can be any place, building, site or structure, which is considered to be of public interest by reason of its historical, archaeological or palaeontological significance.

 

Under section 6 and subject to subsection (4) of the Ordinance, the following acts are prohibited in relation to certain monuments, except under permit;

·     To excavate, carry on building works, plant or fell trees or deposit earth or refuse on or in a proposed monument or monument;

·     To demolish, remove, obstruct, deface or interfere with a proposed monument or monument.

 

The discovery of an Antiquity, as defined in the Ordinance must be reported to the Authority, or a designated person. The Ordinance also provides that, the ownership of every relic discovered in Hong Kong after the commencement of this ordinance shall vest in the Government from the moment of discovery. The Authority on behalf of the government may disclaim ownership of the relic.

 

No archaeological excavation may be carried out by any person, other than the Authority, without a licence issued by the Authority. A licence will only be issued if the Authority is satisfied that the applicant has sufficient scientific training or experience to enable him to carry out the excavation and search satisfactorily, has sufficient staff and financial support.

 

15.1.2   Environmental Impact Assessment Ordinance

The Environmental Impact Assessment Ordinance (EIAO) (Cap. 499) provides additional legislative protection to sites of cultural heritage, which are threatened by development and the Environmental Protection Department is its authority.  The Technical Memorandum contains the guidelines and criteria for the assessment of sites of cultural heritage interest.

 

The CHIA will follow the Antiquities and Monuments Office Criteria for Cultural Heritage Impact Assessment and will fulfill the requirements as set out in Annex 10 and 19 of the Technical Memorandum on EIA Process (EIA Ordinance, Cap. 499, S.16).

 

15.2      Existing/Baseline Condition

15.2.1   Existing development

Many sections of the alignments are situated on existing roads and or/ existing or drainage channels currently under construction. The majority of the alignments are located outside the boundaries of the villages within the study area. The exception to this is the alignment located in Fan Tin Tsuen, San Tin.  The majority of proposed pumping station sites are located on abandoned plots of land outside of the villages.

 

The specific existing impacts for each alignment will be given separately:

(a) Lau Fau San to Mong Tseng Tsuen;

·     Lau Fau San Road

·     Tin Wah Road

·     Nullah running perpendicularly to Tin Wah Road

 

(b) San Tin to Ngau Tam Mei;

·     Ka Lung Road (near Cassino Camp)

·     Kwu Tung Road

·     Village paths in San Tin

·     Castle Peak Road (San Tin and Mai Po)

·     Drainage channel access road between Yau Tam Mei and Nam Sang Wai

·     Reclamations of former pond/marsh areas

 

Yuen Long South (Shap Pat Heung);

·     Shan Ha Tsuen - Tin Tsuen drainage channel

·     Kung Um Road - Nullah along Kung Um Road

·     Sham Chung drainage channel (west of Tai Tong Road) -Nullah and access road

·     Tai Tong Road (northern section) -Tai Tong Road

·     Tai Shu Ha Road East - Nullah and road

 

Yuen Long Effluent Pipeline;

·     Fuk Shun Street (Fung Lok Wai)

·     Tin Wah Road (Tin Shui Wai)

 

15.2.2   Historical Background of the Study Area

Declared Monuments

The following Declared Monuments were identified in the Study Area;

Man Lun Fung Ancestral Hall (San Tin)

 

Graded Buildings

The following Graded buildings have been identified in the Study Area;

Ming Yuen Tong (San Tin) Grade II

Shun Yue Tong (San Tin) Grade I

San Yeh Man Tong (San Tin) Grade II

 

Historical Villages

Lau Fau Shan Road/ Mong Tseng Tsuen

The history of the Lau Fau San area can be traced back many centuries, as a centre of oyster cultivation (Morton 1983). The village today consists of a mixture of commercial/ market and domestic structures, many dating to the 1960’s and 70’s. No resources were recorded in the survey in Lau Fau Shan. Three villages in the study area were found to contain heritage resources, San Hing Wai, Chung Yuen and Mong Tseng Tsuen.

 

San Hing Tsuen

The village of San Hing Wai was settled by members of the Wong clan over 100 years ago. The villagers originally subsisted through the growing of vegetables and rice.

 

Chung Yuen

The settlement is associated with Sha Kong Wai and was settled by members of the Mok clan during the 19th century. The villagers originally grew rice and vegetables to support themselves.

 

Mong Tseng Tsuen

The village of Mong Tseng Tsuen is over two hundred years old. The families associated with it are the Cheng (from Yuen Long) and the Tang, Wong and Lee clans from the neighbouring village of Mong Tseng Wai. All of the villagers originally came from Po On. The villagers grew rice, sweet potatoes and peanuts. They also engaged in fishing. The small well at the edge of the village was abandoned a decade ago.

 

San Tin/ Mai Po

A number of historical villages were located along this alignment. The majority of them were located in San Tin.

 


San Tin

San Tin was originally settled by members of the Man clan during the 14th and 15th centuries. The area was originally considered marginal because of its marshy nature, but later became a rich agricultural area.  San Tin consists of a cluster of villages, centred around Fan Tin Tsuen. The aerial photographs from this area, dating from 2001 (GEO CN30028), show that whilst there are still a number of ponds in the vicinity of the villages, a lot of former agricultural areas have been taken over by light industrial operations, see Figure 15.1.

 

Mai Po Tsuen

Mai Po Tsuen is a small village situated between Castle Peak Road and ponds. The Wong clan is the predominant clan of the village, whose members arrived in the area several hundred years ago, according to local informants. Their ancestral hall “Hin Hing Tong” (AAHB-230) is a modern building. The other clans associated with the village are the, Man, Fung and Chan. These clans share the same gods hall (AAHB-236). All of the settlers came to the area from Guangdong and were Punti. The villagers originally supported themselves through fishing and rice farming.

 

Shap Pat Heung

Thirteen historical villages were located along five alignments in this study area. The alignments were all essentially isolated rural settlements until fairly recent development. This process can be seen in two aerial photographs of the Shap Pat Heung area, dating from 1963 (GEO Y09481), 2002 (GEO CW41000), figures 15.2 and 15.3, respectively. Several villages in the photographs, e.g. Shui Tsui Lo Wai, Tin Liu Tsuen and  Muk Kui Tsuen can also be seen to have contained traditional fung shui features, such as ponds and woods, none of which have survived. The aerial photographs also show that even as late as 1963, the land not occupied by buildings was agricultural in nature. The 2002 photograph shows former fields either overgrown or occupied by new structures.

 

Shan Ha Tsuen

The village of Shan Ha Tsuen was settled by members of the Cheung clan, of Punti origin from Guangdong, approximately 400 years ago. The village was given the name Shan Ha Tsuen, because that was the name of the village in Guangdong from which the settlers originated. The village originally had a moat and fish pond in front of it, both of which were filled in approximately 15 to 20 years ago. The village well, which has been preserved, has been out of use since 1979. The village also previously had a fung shui wood, which was cut down for road construction 15 years ago. There are two cannons placed at the front of the village, which local informants said were used for protection against thieves and the Japanese during the Second World War.

 

Tin Liu Tsuen

The village of Tin Liu Tsuen is a mixed surname Punti village whose inhabitants came to the area approximately 100 years ago. The inhabitants were members of the Wu, Wong, Yip and Sit clans. The villagers supported themselves through rice and vegetable farming.

 

Pak Sha Tsuen

Pak Sha Tsuen is a mixed surname village, whose original inhabitants were of Punti origin from Guangdong. The villagers originally grew vegetables and rice.

 

Muk Kui Tau Tsuen

The village of Muk Kiu Tsuen (‘head of wooden bridge’) was named after a wooden bridge that used to be situated in front of the village. The village was settled by members of the Wu and Chan clans, Punti from Guangdong.

 

Tai Tong Tsuen

Tai Tong Tsuen was settled by members of the Lee and Leung clans, of Punti origins. The villagers originally supported themselves through growing rice and vegetables, for subsistence as well as for sale at the market in Yuen long.

 

Wong Nai Tun Tsuen

This village has been occupied by members of the Ho, Yu and Lai families for five generations. The settlers were originally from Po On province and were of Hakka background. The villagers maintained a similar lifestyle to those of their neighbours in Tai Tong Tsuen, engaging in rice and vegetable cultivation. Collection of wood from the nearby hills was also undertaken by inhabitants of both of these villages.

 

Shui Tsiu San Tsuen

Shui Tsiu San Tsuen is a multi-clan village. The first arrivals were two families of the Wong clan, of Hakka origin. These were the original two houses in the settlement. Later, members of the Lam clan from Fujian arrived and after them, members of the Ching and Yeung and finally, the Cheung. The latter three groups moved here from Shui Tsui Lo Wai. The village originally had a fung shui wood which was cut down to make room for new houses. The villagers supported themselves through farming.

 

Sham Chung Tsuen

Sham Chung Tsuen is a Punti village. It was originally settled by members of the Chan clan, later members of the Kwan, Lam and Yip clans moved there. The villagers originally grew rice as a subsistence crop. The villagers also grew vegetables, which they sold at the Yuen Long market.

 

Shui Tsui Lo Wai

Shui Tsui Lo Wai is a multi-clan Hakka village. The clans associated with it are Kan, Cheung, Chan,Tse, Yeung and Lam. The villagers originally grew vegetables and sweet potatoes which were taken to Hong Kong Island and Yau Ma Tai for sale.

 

Hung Tso Tin

Hung Tso Tin was established by a father and son, named, Kan from Shui Tsui Lo Wai. They were Hakka. The village was named ‘Red Date Field Image’ by a fung shui master. The villagers originally grew vegetables for their own consumption as well as sale at Yuen Long market.

 

Cheng Chu Wai

Cheng Chu Wai was settled by members of the Chan and Tse clans. The village name means green brick village.

 

Nam Hang Tsuen

Nam Hang Tsuen was settled by members of the Cheung clan from the nearby village of Shui Tsui Lo Wai. This settlement dates almost as far back as Shui Tsui Lo Wai. The villagers supported themselves through rice and vegetable farming. The crops were eaten by the villagers and sold at Yuen Long market.

 

Tong Tau Po Tsuen

Tong Tau Po Tsuen was settled by members of the Cheung clan from Guangdong, who were Punti. The villagers originally grew rice which was sold at Yuen long market, but the practice was stopped approximately 20 years ago.

 

Fung Lok Wai

There are three villages located in this area, Tai Tseng Wai, Ng Uk Tsuen and Shing Ka Tsuen. Modern aerial photographs show the area around the villages to be built up.

 

Tai Tseng Wai

The village of Tai Tseng Wai was settled approximately 500 years ago.  There are five surnames associated with the village; Cheng, Leung, Shing, Lam and Tang. All of the families came from Tai Peng, Tung Kwun in Guangdong. The Leung and Cheng families arrived first. The Shing, Lam and Tang arrived about 300 years ago. The people here supported themselves through fishing and farming in the area. Farming was abandoned approximately 20 years ago.

 

Shing Uk Tsuen

The village of Shing Uk Tsuen was settled approximately 400 years ago. It is a single family surname village, i.e. Shing. The families came from Guangdong province. The area behind the village was used to grow crops such as sweet potatoes and peanuts. Many of the men from the villages, traditionally worked abroad.

 


Ng Uk Tsuen

The village of Ng Uk Tsuen is a single surname village, Ng. The 1st generation ancestor was called Ng Hung Lan, who came from Nam Tau. The current generation is the 29th. The Ng family of Ng Uk Tsuen is related to the Shing family of Shing Uk Tsuen by marriage. The villagers supported themselves through farming rice, in rented fields and through fishing and catching crabs in Deep Bay.

 

15.2.3   Geological and topographical background

Lau Fau San/ Mong Tseng Trunk Sewage

The pumping station and alignments run on Pleistocene terraced and Holocene alluvium in Mong Tseng.  The main geology is schistose fine to medium granite.  Pleistocene terraced alluvium extends to Lau Fau San where the main geology is fine to medium granite.

 

Yuen Long Effluent Pipe

The proposed alignment starts at the proposed Yuen Long Sewage Treatment Works Pumping Station, which is situated on 1980’s reclamation.  The alignment then proceeds on Pleistocene terraced alluvium and debris flow deposits.  The lower hill slopes of Wang Chau consist of metasiltstone and phylite with metasandstone.  The alignment will then continue on the reclaimed marine muds of Tin Shui Wai.  North of Tung Tau the alignment will impact on Pleistocene terraced alluvium.  The last stretch to the San Wai Sewage Treatment Works Upgrading runs on Pleistocene debris flow deposits and two outcrops of adasite with tuffs and tuffites connected to block bearing tuff and tuffites.

 

Ngau Tam Mei/ San Tin Trunk Sewerage

The alignment starts on marine muds and continues on to reclaimed land.  Where the alignment meets Castle Peak Road, the geology comprises estuarine deposits.  The alignment branch, which extends to the east into the Ngau Tam Mei area is located on Holocene alluvium.  The alignment, which goes to the north and follows Castle Peak road, is situated on both estuarine deposits and Holocene alluvium. Near the Mai Po archaeological site, the alignment runs on filled land.  The remainder of the alignment, i.e. both sections running north and south near San Tin are situated on a mix of solid geology of coarse ash crystal tuffs and Pleistocene debris flow deposits.

 

Yuen Long South Branch Sewer

The sewer alignments and proposed pumping station locations are located on Pleistocene terraces and Holocene alluvium. 

 

15.2.4   Landform Background of the Study Area

As informed by DSD/SP, there is no existing sewer in the existing site.  The design of the gravity sewers and rising mains have been located away from the existing DSD's stormwater drains, nullah and box culverts.  Therefore, there will be no impact on the existing DSD’s facilities.

 

The following major impacts to the original landforms occur in the Study Areas:

·     Ponds;

·     Utilities;

·     Road cutting; and

·     Nullah.

 

The following tables show the types of impacts, which can be found for each works area:

 

Lau Fau San/ Mong Tseng Trunk Sewage

        

Mong Tseng Tsuen PS

Extent and nature of impacts

General description

5.5m PD, open area in front of rural village; Pleistocene terraced alluvium

Water Supplies Department

No impacts

CLP Power

CLP alignment within the proposed pumping station area

PCCW

telephone cable runs along southern edge of proposed pumping station

Towngas

No impacts

 

Sewer alignment from Mong Tseng to Lau Fau Shan Road

Extent and nature of impacts

General description

on a track along ponds and continuing along the nullah and crossing over an area of former ponds (geology map) to the Tin Wah Road

WSD

water mains are located along the nullah

CLP Power

CLP alignment impacts partly on track and partly on the area of former ponds

PCCW

telephone cable follows the track and crosses the areas of former ponds

Towngas

pipe crosses the former pond area

 

Sewer alignment along Lau Fau Shan Road

Extent and nature of impacts

General description

on Lau Fau Shan Road

WSD

water mains are located on both sides of the Lau Fau Shan Road and Deep Bay Road leading to the Lau Fau Shan PS

CLP Power

CLP alignment runs along both sides of the Lau Fau Shan Road and on the western edge of Deep Bay Road

PCCW

telephone cable runs along both sides of the Lau Fau Shan Road and on the western edge of Deep Bay Road

Towngas

gas pipe runs along the northern edge of Lau Fau Shan Road

 

Lau Fau Shan PS

Extent and nature of impacts

General description

5.3m PD; in open space area to west of Deep Bay Road, western half shows artificially cutting (CLP map); border of Pleistocene terraced alluvium and marine sediments

WSD

water mains cross the proposed pumping station on its eastern half

CLP Power

CLP alignment crosses on the western edge of Deep Bay Road

PCCW

telephone cable crosses on the western edge of Deep Bay Road

Towngas

no impacts

 

Yuen Long Effluent Pipe

              YLEPS

Areas of impacts

general description

1982 Reclamation

Water Supplies Department

no impacts

CLP Power

no impacts

PCCW

no impacts

Hutchison Global Crossing

no impacts

 

Sewer alignment from YLEPS to Wang Chau

Areas of impacts

general description

3.5 to 5.4m PD.; Sewer alignment runs firstly on reclamation after which it follows the road between the historic villages of Tai Tseng Ng Uk Tsuen, Tai Tseng Wai and Shing Uk Tsuen; Pleistocene terraced alluvium and debris flow deposits

WSD

water mains follow the road

CLP Power

no impacts

PCCW

impacts on most parts of the road

Hutchison Global Crossing

no impacts

 

Sewer alignment on Wang Chau

Areas of impacts

general description

Between 36 and 20m PD.; relatively undisturbed patches of lower hill slopes; metasiltstone and phylite with meta sandstone

WSD

no impacts

CLP Power

no impacts

PCCW

no impacts

Hutchison Global Crossing

no impacts

 

Sewer alignment from Wang Chau across Tin Shui Wai to Tung Tau Tsuen

Areas of impacts

general description

Reclaimed former marine muds

WSD

water mains follow the proposed alignment

CLP Power

no impacts

PCCW

cable follows proposed alignment

Hutchison Global Crossing

cable follows proposed alignment

 

 

Sewer alignment north of Tung Tau Tsuen

Areas of impacts

general description

Approximately 5m. PD.; north of a hillock; open storage areas and temporary structures; Pleistocene terraced alluvium; part of the alignment falls within the Tung Tau Tsuen Archaeological boundary site.

WSD

no impacts

CLP Power

part impacts near the temporary structures

PCCW

part impacts near the temporary structures

Towngas

no impacts

 

Sewer alignment from north of Tung Tau Tsuen to San Wai STW Upgrading

Areas of impacts

general description

Approximately 10m PD.; open storage areas temporary structures; wet and low-lying area

WSD

no impacts

CLP Power

part impacts on the proposed alignment

PCCW

no major impacts

Towngas

no impacts

 

San Wai STW Upgrading

Area of impacts

general description

Below 10m PD.; container storage areas, but mainly situated on pond area (to north of existing plant); proposed works fall within the archaeological site boundary

WSD

existing plant

CLP Power

no impacts

PCCW

no impacts

Towngas

no impacts

 

Ngau Tam Mei/ San Tin Trunk Sewerage

 

Sewer alignment from Kam Tin River to Ngau Tam Mei SPS

Extent and nature of impacts

General description

on area of former ponds and estuarine sediments

WSD

no impacts

CLP Power

no impacts

Hutchison Global Crossing

no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

no impacts

 

Ngau Tam Mei SPS

Extent and nature of impacts

General description

on area of former ponds and estuarine sediments

WSD

no impacts

CLP Power

no impacts

Hutchison Global Crossing

no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

no impacts

 

Sewer alignment from Ngau Tam Mei SPS to Tam Mei Camp SPS

Extent and nature of impacts

General description

the sewer alignment crosses San Tam Road and then runs immediately along a channel currently under construction by TTD; the area consists of ponds or river channel

WSD

the sewer alignment will follow the water mains in this area

CPL Power

no impacts

Hutchison Global Crossing

no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

no impacts

 

Tam Mei Camp SPS

Extent and nature of impacts

General description

within the river channel and its immediate riverbank to the south

WSD

no impacts

CLP Power

no impacts

Hutchison Global Crossing

no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

no impacts

 

Sewer alignment from Ngau Tam Mei SPS to San Tin SPS

Extent and nature of impacts

General description

entirely on Castle Peak Road

WSD

the sewer alignment will follow the water mains in this area

CLP Power

Existing (and proposed) cable follows the sewer alignment starting approximately opposite the Maple Gardens and continues until opposite the Mai Po Village area; the cable continues to run parallel with the sewer alignment from Mai Po San Tsuen until the alignment leaves Castle Peak Road

Hutchison Global Crossing

plant follows the proposed sewer alignment along Castle Peak Road

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

cable runs along proposed sewer alignment on Castle Peak Road starting approximately opposite a fly-over crossing the Yuen Long Highway before the village of Tsing Lung Tsuen

 

San Tin SPS

Extent and nature of impacts

General description

on former marine sediments

WSD

water mains border the proposed pumping station

CLP Power

no impacts of existing cable; proposed cable will be located at southern end of proposed pumping station

Hutchison Global Crossing

no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

no impacts

 

Sewer alignment from San Tin SPS to San Lung Tsuen SPS

Extent and nature of impacts

General description

continues on Castle Peak Road and then turns north along the lower slopes of hillock to the debris flow deposits on which the historic village of San Tin was built

WSD

the sewer alignment will follow the water mains in this area

CLP Power

cable runs same alignment on Castle Peak road as proposed sewer alignment; further no impacts

Hutchison Global Crossing

plant follows the proposed sewer alignment along Castle Peak Road; no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

cable runs along the Castle Peak Road

 

Fan Tin Tsuen SPS

Extent and nature of impacts

General description

Maximum of 3m PD; Pleistocene debris flow deposits

WSD

the proposed pumping station will include existing water mains

CLP Power

no impacts

Hutchison Global Crossing

no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

no impacts

 

Sewer alignment from San Lung Tsuen SPS to Casino Line SPS

Extent and nature of impacts

General description

the alignment continues on Castle Peak Road and turns off southeast on Kwu Tung Road and Ka Lung Road until it reaches the existing sewerage plant

WSD

the sewer alignment will follow the water mains in this area

CLP Power

the only impacts are located on Castle Peak Road

Hutchison Global Crossing

no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

no impacts

 

Cassino Line  SPS

Extent and nature of impacts

General description

within existing sewage treatment plant

WSD

connects with military main and continues to the existing sewage treatment plant

CLP Power

no impacts

Hutchison Global Crossing

no impacts

Cable TV

no impacts

Towngas

no impacts

Warf New T&T

no impacts

 


Yuen Long South Branch Sewer

 

Shan Ha Tsuen SPS

Extent and nature of impacts

General description

9.3m PD; open space area in front of Shan Ha Tsuen Village

WSD

no impacts

CLP Power

cables are located on the eastern edge of the proposed pumping station

PCCW

no impacts

Towngas

no impacts

 

Sewer alignment connected to Sha Ha Tsuen SPS

Extent and nature of impacts

General description

sewer alignment crosses alluvial plain to the river; then continues following the river to the north; the alignment subsequently follows the artificial cut of the Yuen Long Highway up to Kung Um Road

WSD

no impacts

CLP Power

no impacts

PCCW

no impacts

Towngas

no impacts

 

Alternative Sewer alignment connected to Sha Ha Tsuen SPS

Extent and nature of impacts

General description

sewer alignment crosses alluvial plain to the river; then continues following the river to the north; the alignment subsequently crosses Yuen long Highway and continues east along an area occupied with structures

WSD

partial impact by existing water mains

CLP Power

partial impact by CLP cables

PCCW

partial impact by telephone cables

Towngas

no impacts

 

Muk Kiu Tau Tsuen SPS

Extent and nature of impacts

General description

7.9m PD; open space area to the north of historic village of Muk Kiu Tau Tsuen; Pleistocene alluvial terrace

WSD

no impacts

CLP Power

cable is located at the western edge of the proposed pumping station

PCCW

cable runs along western edge of proposed pumping station

Towngas

no impacts

 

Sewer alignment extending north of Muk Kiu Tau Tsuen SPS and extending south towards Pak Sha Tsuen SPS

Extent and nature of impacts

General description

one sewer branch alignment extends north to the Yuen Long Highway along an existing nullah; another branch extends south  along same nullah to the Pak Sha Tsuen SPS

WSD

existing water mains located at proposed sewer alignment

CLP Power

cable along the proposed sewer alignment and stops just south of Muk Kiu Tau Tsuen

PCCW

cable located at proposed sewer alignment

Towngas

no impacts

 

Pak Sha Tsuen SPS

Extent and nature of impacts

General description

12.3m PD; located to the north of the historical village of Pak Sha Tsuen; Pleistocene terraced alluvium

WSD

no impacts

CLP Power

no impacts

PCCW

no impacts

Towngas

no impacts

 

 

 

Sewer alignment extending south from Pak Sha Tsuen SPS

Extent and nature of impacts

General description

sewer alignment runs south along an existing nullah

WSD

existing water mains located at proposed sewer alignment

CLP Power

cable located along proposed sewer alignment

PCCW

cable located along proposed sewer alignment

Towngas

no impacts

 

Sham Chung Tsuen SPS

Extent and nature of impacts

General description

8.9m PD; Holocene alluvium

WSD

no impacts

CLP Power

no impacts

PCCW

no impacts

Towngas

no impacts

 

Sewer alignment extending north of Sham Chung Tsuen SPS and between the above station and Shui Tsiu San Tsuen SPS

Extent and nature of impacts

General description

sewer alignment extending north of the proposed pumping station following a river; the alignment continues to follow the river south to the proposed Shui Tsiu San Tsuen SPS

WSD

no impacts

CLP Power

no impacts

PCCW

no impacts

Towngas

no impacts

 

Shui Tsiu San Tsuen SPS

Extent and nature of impacts

General description

located in a former pond (PCCW map)

WSD

no impacts

CLP Power

no impacts

PCCW

no impacts

Towngas

no impacts

 

Sewer alignment extending south of Shui Tsiu San Tsuen SPS

Extent and nature of impacts

General description

alignment continues to follow the river

WSD

no impacts

CLP Power

no impacts

PCCW

no impacts

Towngas

no impacts

 

Tai Tong Road Sewer alignment

Extent and nature of impacts

General description

sewer alignment located along Tai Tong Road

WSD

existing water mains are located at proposed sewer alignment

CLP Power

two smaller areas of impact at the southern end of this alignment

PCCW

cable located at proposed sewer alignment

Towngas

no impacts

 

Shung Ching San Tsuen SPS along Tai Tong Road

Extent and nature of impacts

General description

9.2m PD; open space area; Pleistocene terraced alluvium

WSD

no impacts

CLP Power

no impacts

PCCW

no impacts

Towngas

no impacts

 

Tai Shui Ha Road Sewer alignment

Extent and nature of impacts

General description

sewer alignment runs along an existing nullah

WSD

water mains are located along proposed alignment

CLP Power

impacts occur from Nga Yiu Tau SPS to the same height as split of nullah towards the south

PCCW

cable located at proposed sewer alignment

Towngas

no impacts

 

Nga Yiu Tau SPS

Extent and nature of impacts

General description

approximately 12.3m PD (nearest indication of PD height) ; open space with building located in center of proposed pumping station; Holocene alluvium

WSD

no impact

CLP Power

cable runs through proposed pumping station (east-west direction)

PCCW

no impacts

Towngas

no impacts

 

15.2.5   Archaeological background of the study area

The proposed works, except for Tung Tau Tsuen will not impact directly on a known archaeological site (AMO-files).  Known archaeological sites, however, can be found in the vicinity of the works and are briefly described below.  The works at Tung Tau Tsuen will partly impact within the boundary of the known archaeological site, field evaluation will identify the nature of the archaeological deposits.

 

Lau Fau San/ Mong Tseng Trunk Sewage

·     Mong Tseng (Neolithic, Bronze and Historical Period)

·     Lau Fau San (Neolithic and Bronze period)

 

Yuen Long Effluent Pipe

·     Tung Tau Tsuen Archaeological Site: Ming and Qing Dynasty findings and a Song Dynasty sherd (AMO-files); The boundary of the archaeological site is marked on Figure 15.45.

·     Tseung Kong Wai So Kwun Tsai Archaeological Site: Finding dating to Late Neolithic, Bronze Age and Song Dynasty have been recovered (AMO-files).

 

Ngau Tam Mei/ San Tin Trunk Sewerage

·     Mai Po (Historical Period)

·     Ngau Tam Mei Tsuen South, Sun Hing Farm (Bronze and Historical Period)

 

Yuen Long South Branch Sewer

·     Yuen Leng, Kong Tau Tsuen (Bronze Period)

 

15.3      Assessment Methodology for Construction Phase

15.3.1   Assessment Approach for Built Heritage

The assessment methodology for the construction phase will include impacts arising from the proposed alignments as well as the proposed pumping stations.  The following assessment methodology was used:

 

1) A desk-based study was conducted to determine the presence of historical occupation of the study area and to assess the potential for built heritage resources to still be present. The study included information gathered from the following sources; the Antiquities and Monuments Office published and unpublished papers and studies; publications on relevant historical, anthropological and other cultural studies; unpublished archival, papers, records; collections and libraries of tertiary institutions; historical documents which can be found in Public Records Office, Lands Registry, District Lands Office, District Office, Museum of History; cartographic and pictorial documentation.

 

2) A field survey was conducted in all areas where built heritage potential was established and existing information was not conclusive for purposes of the assessment. The scope of the survey covered the study corridor as well as areas within close proximity to it, which was defined as being a distance of 100 metres on either side. The heritage features included in the survey consisted of the following:

·     Built features (excluding graves) constructed prior to 1950

·     Built features constructed post 1950, but deemed to possess cultural or historical significance

·     Clan graves dating prior to the Second World War

·     Cultural landscape features, such as fung shui woods or ponds

·     Historical landscape features, such as agricultural field patterns, terraces, paths and trackways and ponds

 

The field survey incorporated the following methodology:

 

Built Features

The survey consisted of a field evaluation incorporating the collection of photographic, oral and written information, on the architecture and history of all structures that may be impacted by the proposed works. This information was hand recorded in the field. The information collected in the field survey was then entered onto type written forms for inclusion in the report. The design of the forms is based on AMO and ICOMOS (International Charter for the Conservation and Restoration of Monuments and Sites) standards for the recording of historical resources with modifications to suit architectural styles and situations encountered in Hong Kong. The forms have also been designed to provide details of all identified resources, including written descriptions of each recorded feature, including; age, details of architectural features, condition, past and present uses, an architectural appraisal, notes on any modifications, direction faced and associations with historical/ cultural events or individuals. They also include a photographic record of each building or structure including the exterior (the elevations of all faces of the building premises, the roof, close up for special architectural details) and the interior (special architectural details) where possible, as well as the surroundings of the feature. The location of each feature has also been highlighted on a 1:1000 scale map. A description of the surrounding environment has also been included as part of the survey.

 

Graves

Pre-war clan graves were also included as part of the survey and were recorded on field recording forms, which include a written description, a photographic record, a copy of the inscription and the dimensions. Their locations have also been highlighted on a 1:1000 scale map. It should be noted that there are graves located within the Cassino Camp itself, which were not accessible as part of the survey. The graves lie a minimum distance of 10 metres from the works area, however and are separated from it by a chain link fence. There will be no impact to these graves and further investigation will not be necessary.

 

Cultural and Historical Landscape Features

A written description of each recorded feature has been made, including information gathered from interviews with local informants. The location of each recorded feature has been highlighted on a 1:1000 scale map and a photographic record of each identified feature made.

 

15.3.2   Assessment Approach for Archaeology

Desk-based research is undertaken to identify areas of original landform with archaeological potential, which have not been impacted by previous excavations.  The desk-based research will also highlight known archaeological sites both within the proposed works areas and in the vicinity.

The identified areas of potential will be assessed by a field evaluation programme; comprising of field scan, auger testing programme and test pit excavations.  The field evaluation programme will be endorsed by the Antiquity Authorities. 

 

Identified areas of archaeological potential currently inaccessible due to concrete or asphalt cover or private land issues will have to be assessed after land resumption or during a programme of archaeological monitoring during the construction phase.

 

15.4      Results of the desk-based Study

15.4.1   Built Heritage (Baseline)

The baseline study confirmed that the Study area contained historical potential and that there was not sufficient information available to assess the potential impacts from the proposed works, therefore a field survey was carried out, the results of which are presented in Section 15.3.4.

 

15.4.2   Archaeology

The table below presents the results of the desk-based study in which the areas of archaeological potential were identified.  Please note that no assessment was undertaken for the Yuen Long sewage treatment works effluent pipeline, Conforming scheme of 2A-IT as shown on Figure 1.4 as it is not the preferred option.  An Impact Assessment for archaeology should be undertaken if this alignment is chosen.

 

Lau Fau San/ Mong Tseng Trunk Sewage

        

Mong Tseng Tsuen PS

archaeological potential of landform and relatively undisturbed

Sewer alignment from Mong Tseng to Lau Fau Shan Road

no archaeological potential (cumulative impacts of utilities; along existing nullah; area of former ponds)

Sewer alignment along Lau Fau Shan Road

no archaeological potential (road with cumulative impacts of utilities)

Lau Fau Shan PS

no archaeological potential (cumulative impacts of utilities and cutting)

 

Yuen Long Effluent Pipe

        

Works areas

Archaeological potential

YLEPS

no archaeological potential [former pond area]

Sewer alignment from YLEPS to Wang Chau

no archaeological potential [reclamation] except for the portion of the road which runs in between the historical villages

Sewer alignment on Wang Chau

some portions of the lower hill slopes appear relatively undisturbed and have archaeological potential

Sewer alignment from Wang Chau across Tin Shui Wai to Tung Tau Tsuen

no archaeological potential [reclamation]

Sewer alignment north of Tung Tau Tsuen

Although believed to be low in archaeological potential due to the low-lying nature of the area, part of the alignment will fall within the boundary of the Tung Tau Archaeological Site and requires therefore further testing

Sewer alignment from north of Tung Tau Tsuen to San Wai STW Upgrading

no archaeological potential [low-lying-wet area]

San Wai STW Upgrading

Although the proposed works will impact inside the boundary of the Tseung Kong Wai So Kwun Tsai Archaeological Site, the works will impact on ponds and has therefore no longer archaeological potential

 

Ngau Tam Mei/ San Tin Trunk Sewerage

 

Sewer alignment from Kam Tin River to Ngau Tam Mei SPS

no archaeological potential (former ponds and estuarine sediments)

Ngau Tam Mei SPS

no archaeological potential (former ponds and estuarine sediments)

Sewer alignment from Ngau Tam Mei SPS to Tam Mei Camp SPS

no archaeological potential (river meandering and ponds)

Tam Mei Camp SPS

 

no archaeological potential (river meandering)

Sewer alignment from Ngau Tam Mei SPS to San Tin SPS

 

no archaeological potential (road with cumulative impacts of utilities)

San Tin SPS

 

no archaeological potential (marine sediments)

Sewer alignment from San Tin SPS to San Lung Tsuen SPS

 

no archaeological potential (road and cumulative utilities impact)

Fan Tin Tsuen SPS

 

no archaeological potential (low-lying and existing water mains impacts)

Sewer alignment from San Lung Tsuen SPS to Casino Line SPS

 

no archaeological potential (road alignment and cumulative impacts of utilities)

Cassino Line SPS

no archaeological potential within existing sewerage treatment plant

 

Yuen Long South Branch Sewer

 

Shan Ha Tsuen SPS

archaeological potential of landform and relatively undisturbed

Sewer alignment connected to Sha Ha Tsuen SPS

no archaeological potential (floodplain; meandering river and road cutting)

Alternative Sewer alignment connected to Sha Ha Tsuen SPS

no archaeological potential (floodplain; meandering river and area of housing)

Muk Kiu Tau Tsuen SPS

archaeological potential of landform and relatively undisturbed

Sewer alignment extending north of Muk Kiu Tau Tsuen SPS and extending south towards Pak Sha Tsuen SPS

no archaeological potential (along existing nullah with cumulative impacts of utilities)

Pak Sha Tsuen SPS

archaeological potential of landform and relatively undisturbed

Sewer alignment extending south from Pak Sha Tsuen SPS

no archaeological potential (along existing nullah with cumulative impacts of utilities)

Sham Chung Tsuen SPS

no archaeological potential (Holocene alluvium)

Sewer alignment extending north of Sham Chung Tsuen SPS and between the above station and Shui Tsiu San Tsuen SPS

no archaeological potential (river meandering)

Shui Tsiu San Tsuen SPS

no archaeological potential (former pond area)

Sewer alignment extending south of Shui Tsiu San Tsuen SPS

no archaeological potential (river meandering)

Tai Tong Road Sewer alignment

no archaeological potential (cumulative impacts of road and utilities)

Shung Ching San Tsuen SPS along Tai Tong Road

archaeological potential of landform and relatively undisturbed

Tai Shui Ha Road Sewer alignment

no archaeological potential (cumulative impacts of road construction and utilities )

Nga Yiu Tau SPS

no archaeological potential (Holocene alluvium)

 

The information was presented to the Antiquities and Monuments Office and on the basis of this information the methodology was agreed.  The table below shows the endorsed methodology.

 


Lau Fau San/ Mong Tseng Trunk Sewage

        

Works areas

Proposed methodology

Mong Tseng Tsuen PS (Figure 15.44)

Field scan

Minimum of 10 auger hole tests

One test pit excavation

Sewer alignment from Mong Tseng to Lau Fau Shan Road

no action required

Sewer alignment along Lau Fau Shan Road

no action required

Lau Fau Shan PS

no action required

 

Yuen Long Effluent Pipe

        

Works areas

Proposed methodology

YLEPS

no action required

Sewer alignment from YLEPS to Wang Chau

no action required at this stage; Archaeological monitoring of the excavation works near the historical villages will be required.

Sewer alignment on Wang Chau (Figure 15.43)

Field scan of the entire area

a minimum of 20 auger hole tests

Two test pits

Sewer alignment from Wang Chau across Tin Shui Wai to Tung Tau Tsuen

no action required

Sewer alignment north of Tung Tau Tsuen (Figure 15.45)

Field scan of the entire area

a minimum of 20 auger hole tests

Two test pits

(currently occupied by villager and landowner issues may arise)

Sewer alignment from north of Tung Tau Tsuen to San Wai STW Upgrading

no action required

San Wai STW Upgrading

no action required

 

Ngau Tam Mei/ San Tin Trunk Sewerage

 

Works areas

Proposed methodology

Sewer alignment form Kam Tin River to Ngau Tam Mei SPS

No action required

Ngau Tam Mei SPS

no action required

Sewer alignment from Ngau Tam Mei SPS to Tam Mei Camp SPS

no action required

Tam Mei Camp SPS

no action required

Sewer alignment from Ngau Tam Mei SPS to San Tin SPS

no action required

San Tin SPS

no action required

Sewer alignment from San Tin SPS to San Lung Tsuen SPS

no action required

Fan Tin Tsuen SPS

no action required

Sewer alignment from San Lung Tsuen SPS to Casino Line SPS

no action required

Cassino Line  SPS

no action required

 

Yuen Long South Branch Sewer

 

Works areas

Proposed methodology

Shan Ha Tsuen SPS (Figure 15.46)

Field scan

Minimum of 10 auger hole tests

One test pit excavation

Sewer alignment connected to Sha Ha Tsuen SPS

no action required

Alternative Sewer alignment connected to Sha Ha Tsuen SPS

no action required

Muk Kiu Tau Tsuen SPS

no action required

Sewer alignment extending north of Muk Kiu Tau Tsuen SPS and extending south towards Pak Sha Tsuen SPS

no action required

Pak Sha Tsuen SPS

no action required

Sewer alignment extending south from Pak Sha Tsuen SPS

no action required

Sham Chung Tsuen SPS

no action required

Sewer alignment extending north of Sham Chung Tsuen SPS and between the above station and Shui Tsiu San Tsuen SPS

no action required

Shui Tsiu San Tsuen SPS

no action required

Sewer alignment extending south of Shui Tsiu San Tsuen SPS

no action required

Tai Tong Road Sewer alignment

no action required

Shung Ching San Tsuen SPS along Tai Tong Road (Figure 15.47)

Field scan

Minimum of 10 auger hole tests

One test pit excavation

Tai Shui Ha Road Sewer alignment

no action required

Nga Yiu Tau SPS

no action required

 

15.5      Results of Built Heritage Survey (Construction Phase)

15.5.1   Built Features

A large number of resources were identified in the field survey. The information for each structure recorded in the field survey has been put into table form and can be found in Appendix 15.1. The majority of the structures were located within the boundaries of historical villages. As part of the field survey, the setting and surroundings of each village was noted, the information that was gathered is presented below. The figure number corresponding to the map illustrating the location of each of the recorded resources is also provided in the text.

 

Lau Fau Shan Road/ Mong Tseng Tsuen

(a)San Hing Wai (Figure 15.4)

The village is set facing Lau Fau Shan Road and is situated at the base of and on lower hill slopes rising eastwards. The village is currently backed by a lychee orchard.  Today the village consists of a mixture of historical and modern buildings. Replacement of older buildings is ongoing as was evidenced by construction works noted during this field survey. The village paths and domestic drainage outlets are concrete, but in places the original stone features could be seen to have simply been covered by concrete rather than replaced. The majority of the recorded houses were either in use as residences or being used for holding a family shrine or for general storage. The predominant type of recorded structures were green brick courtyard style terrace houses. The majority of these houses were relatively unaltered on their exteriors and still had decorative canopies over their entranceways. The bricks in the structures were for the most part a uniform pale green to grey colour and long and narrow in shape. There was no standard bonding pattern noticeable.

 

(b) Chung Yuen(Figure 15.5)

Chung Yuen consists of a small number of houses to the west of Sha Kong Wai village. It consists mainly of modern village housing. The only historical structures are a green brick terrace row and single end terrace unit.

 

The village of Sha Kong Wai did not fall within the study area. There was, however, a Tin Hau temple associated with the village, located about 100 metres to its east that did fall within the study area. The temple and its associated shrine can be found on Figure 15.6. A recently constructed Kwun Yum statue was also located nearby and it can be found on Figure 15.7 

        

(c) Mong Tseng Tsuen (Figure 15.8)

Mong Tseng Tsuen is located on a hill slope and contained examples of stone terracing, especially at the rear of the village leading up to a fung shui wood. Twenty-two of the twenty-five recorded features were green brick courtyard terrace units. Four of these structures were ruins. The remaining structures were for the most part abandoned or being used for storage. Stone lined drains were still in use parts of the village, although concrete drains were also present.

 

San Tin / Mai Po

(a) San Tin (Figure 15.9)

Three villages fell within the study area for the project, San Lung, Tsuen, on Lung Tsuen and Fan Tin Tsuen. The latter is the centre of the settlement and contains a number of culturally important buildings, including a Declared Monuments, Man Lun Fung Ancestral Hall. The surveyed villages also contained a number of other historical buildings, although the majority of older buildings have been replaced by modern villages blocks. The majority of these structures were courtyard terrace style green brick houses. A number of these houses were inhabited. Many of the green brick units also had stone elements integrated into their structures, i.e. courses of cut granite along the lower portions of their walls, granite corner stones and carved door and gate frames, threshold stones and lintels.

 

(b) Mai Po Tsuen (Figure 15.10)

The majority of the houses in the village are modern, with only six historical houses found to still be standing. These houses were all green brick courtyard style terrace units. Their condition was generally poor with no evidence of regular maintenance. The bricks ranged from green to grey to pale brown. Bricks in several of the structures were heavily eroded. The local inhabitants informed that they refer to the entire village as Mai Po Tsuen, even though they are given two names on the 1:1000 scale map, i.e. Mai Po Lo Wai and Mai Po San Tsuen. The Yeung Hau Kung temple (AAHB-227) is also found on this figure.

 

(c) Yau Mei San Tsuen (Figure 15.11)

Yau Mei San Tsuen is not an historical village having been settled post 1950. The shrine associated with the village was reconstructed in 1975.

 

Shap Pat Heung

(a) Shan Ha Tsuen (Figure 15.12)

The village contains a large number of historical buildings, including domestic structures and study halls (each branch of the clan has their own study hall). The ancestral hall of the village has been restored in traditional style. The majority of domestic structures were courtyard style terrace houses of green brick. The majority of these buildings were relatively unaltered externally and retained decorative features. The majority of brick structures contained dark green to pale grey bricks. The paler bricks could be seen in several instances to be suffering from various degrees of erosion. Many of the houses, both old and new had a traditional shrine consisting of a stone placed in concrete with an incense holder in front.

 

(b) Tin Liu Tsuen (Figure 15.13)

The village is set on flat land and there was no evidence of a fung shui wood in the vicinity. The village gate and temple were both of traditional green brick construction. The majority of recorded resources were green brick terrace units. The majority of bricks were pale green grey in colour. Several of the structures contained concrete parapets on their facades, having had their decorative canopies removed.

 

(c) Muk Kiu Tau Tsuen (Figure 15.14)

The majority of structures in this village were modern, but at least ten years old. The village gate and ancestral hall of the Wu family are traditional green brick structures. The majority of bricks used in the structures were dark green in colour and in good condition.

 

(d) Pak Sha Tsuen (Figure 15.15)

Unlike the two nearby villages of Tin Liu Tsuen and Muk Kiu Tsuen, the gate of this village is of modern construction. Only a small number of structures were recorded in the village. The condition of many of these was very poor with almost half being ruinous. There were three examples of courtyard style terrace units remaining in the village.

 

(e) Tai Tong Tsuen (Figure 15.16)

The majority of the structures in the village were modern. The older buildings were for the most part abandoned or being used for storage. The area at the back of the village contained the ruins of a large study hall. There were several new buildings under construction at the time of the survey.

 

(f) Wong Nai Tun Tsuen (Figure 15.17)

This small village contained a higher percentage of older buildings than many of the other recorded villages. The houses ranged from large green brick, two storey structures to simple single storey, single room terrace units.

 

(g) Shui Tsiu San Tsuen (Figure 15.18 and 15.19)

The village contains a large number of ancestral halls, reflecting the different clans associated with the village. The ancestral halls are of similar architectural style, relatively undecorated façade with piers at both sides, open entrance hall and main hall. The gate of the village also reflects this style. The recorded houses of the village were constructed of green brick. They were not of a single architectural style. The majority of the structures in the village dated to the 1960’s and 70’s.

 

(h) Sham Chung Tsuen (Figure 15.20)

Again the majority of buildings in this village were modern. The older houses were for the most part, green brick courtyard style terrace units. Most of these buildings still had a decorative canopy over the entranceway. The bricks used in the structures varied from dark green to pale grey. The houses also contained examples of cut granite elements, such as corner stones, door frames and threshold stones.

 

(i) Shui Tsui Lo Wai (Figure 15.21)

The large number of clans associated with the village is reflected in the large number of ancestral halls found there. The majority of the halls have been rebuilt. As with most of the surveyed villages the majority of structures here were modern.

 

(j) Hung Tso Tin (Figure 15.21)

The village contains very few older structures. These were mostly houses, constructed of green brick and lacking any decorative features. The ancestral hall was rebuilt ten years ago. The village well ceased to be used about a decade ago.

 

(k) Cheng Chun Wai (Figure 15.22)

Very little of the traditional village still remains, apart from a disused well and village gate in very poor condition. The rest of the village is completely modern and does not contain a traditional layout.

 

(l) Nam Hang Tsuen (Figure 15.23)

The recorded structures in the village consisted of houses and a Kwun Yum hall. The houses were for the most part green brick terrace units with various degrees of modification.

 

(m) Tong Tau Po Tsuen (Figure 15.24)

The village has very few historical buildings, with only four house units being recorded. These were green brick terrace in style.

 

The village of Nga Yiu Tau does not contain a traditional layout and only contained a shrine and a green brick terrace row, Figure 15.25. The Tai Shu Ha Tin Hau temple is also located along to the north east of the village and is also shown in Figure 15.25.

 

(n) Shung Ching San Tsuen

Shung Ching San Tsuen does not contain a traditional village layout. There are several examples of mansions scattered throughout the area, the oldest remaining one, ‘Yau Lo’ (AAHB-213) being built in 1936, Figure 15.26. A church built in the 1930’s is also located on this map. Other mansions (AAHB-208, 209 and 210),  Figure 15.27. These structures are very grand in style and contain numerous decorative architectural features. The area was originally inhabited for the most part, by Hakka people from Mui Yuen. The area was traditionally associated with the village of Hung Tso Tin. It was given the name Shung Ching San Tsuen approximately 30 years ago. The Shung Ching Public School (AAHB-215) was built in 1950, see Figure 15.28.

 

The locations of a gate and road inscription plaque (AAHB-211 and 212) can be seen on Figure 15.29, a shrine (AAHB-207) on Figure 15.30. An ancestral hall located on Tai Shu Ha Road West (AAHB-216) is shown in Figure 15.31.

 

Fung Lok Wai

(a) Tai Tseng Wai (Figure 15.32)

This village contained a number of older buildings. The majority of them were terrace houses, constructed of brick with no decorative features and a single pitched roof. The houses often had foundations of uncut or very roughly cut stones. A number of the houses were abandoned, used only for storage or housing family shrines. The traditional houses that were still being occupied often had alterations such as window additions, modern doors/gates and air conditioner units. As was seen in the village of Shing Uk Tsuen, most of the replacement village houses appear to have been constructed during the 1960’s and 1970’s.

 

(b) Shing Uk Tsuen (Figure 15.32)

This village contains a number of traditional structures. Many of the domestic structures were courtyard style terrace units.  The majority of these structures were either abandoned or closed up and not being used as houses. Many of the modern replacement structures date to the 1970’s and 1980’s. There is no current building activity going on in the village. There are still a number of cut stone pieces, taken from demolished buildings, in the village.

 

(c) Ng Uk Tsuen  (Figure 15.33)

This village contained a number of traditional structures in various conditions, although many of the older houses were abandoned or ruinous. The majority of replacement buildings in the village were at least ten years old and there was no evidence of ongoing construction. The area behind the village contained a fung shui wood.

 

The location of a shrine located on Fuk Shing Street can be seen on Figure 15.32.

 

Buddhist Blessing Stones

Twenty-four (indicated as B01 through B024 in this report) of these stones were identified in the field survey. All of the stones consist of a rectangular engraved granite block. As the basic form of the stones is the same, individual recording forms were not employed in the survey. Instead photographs of each stone have been included in Appendix 15.2 and the locations of the stones can be found on the following figures:

·     B01, B02 and B03 (Figure 15.4)

·     B04 and B05 (figure 15.5)

·     B06 (Figure 15.20)

·     B07 (Figure 15.21)

·     B08 (Figure 15.30)

·     B09 (Figure 15.30)

·     B10, B11, B12 , B13, B14 and B15 (Figure 15.10)

·     B16 (Figure 15.31)

·     B17 (Figure 15.26)

·     B18 and B19 (Figure 15.34)

·     B20 (Figure 15.35)

·     B21 (Figure 15.36)

·     B22, B23 and B24 (Figure 15.11)

 

15.5.2   Graves

1:1000 scale maps of the study areas indicated that there were graves located in several areas. The field survey confirmed that the majority of graves were modern. The following historical graves were identified in the grave survey, (catalogue, including photographs and inscriptions, is included in this report in Appendix 15.3).

 

(a) Mong Tseng Tsuen (Figure 15.37)

YLKT-G01         Brick and concrete enclosure, in very poor condition, inscription obscured.

YLKT-G02         Two graves of the Cheung family. Last renovated during the Qing Dynasty, untended. Majority of inscription indiscernible. Concrete and brick construction.

YLKT-G03         Stone and concrete circular enclosure, inscription unreadable, untended.

 

(b) San Tin Park (Figure 15.38)

YLKT-G04         Concrete enclosure, over 100 years old according to local informants. Man family. Renovated in 1987. Modern structure.

 

(c) Kah Lung Road (Figures 15.39,15.40, 15.41 and 15.42 )

YLKT-G05         Concrete enclosure, last renovated 1984 (previously 1858), modern features. Man family.    

YLKT-G06         Concrete, over brick, enclosure with red and green decoration. Man family.

Renovated in 1962, modern features.

YLKT-G07         Concrete enclosure with pebble finish. Renovated in 1991. Man family.

YLKT-G10         Modern large concrete enclosure, pebble finish with red trim. Man and Law families.

YLKT-G11         Large concrete enclosure, pebble finish with red trim. Renovated in 1988. Man clan.

YLKT-G12         Concrete grave enclosure, modern features, original grave dating back to the Ming Dynasty. Man clan

YLKT-G13         Concrete enclosure. Red steps. Man clan. No renovation date.

YLKT-G14 A: Double grave, concrete, renovated in 1998. Modern features, originally dated to Qing Dynasty. B: Same style as A, renovated in 1954, man clan. Modern features.

YLKT-G15         Concrete enclosure with red and blue design above inscription. Man clan, renovated in 1954. Modern features.

YLKT-G16         Concrete enclosure with red rounded pattern over inscription. Qing renovation noted (1774), modern features, renovation date not noted.

YLKT-G17         Concrete enclosure with red decoration. Man clan. Modern features, brick underneath concrete visible in cracks.

YLKT-G18 A to F          A series of renovated graves dating originally back to the Ming and Qing period. Concrete enclosures, modern features. Man clan.

YLKT-G19         Concrete enclosure with semi-circular platform. Modern features, renovated 1946. Man clan.

 

15.5.3   Cultural and Historical Landscape Features

As noted earlier, the aerial photographs showed that many of the villages traditionally contained fung shui woods and ponds. The field survey confirmed that the vast majority of these features are no longer in existence. Local informants noted that most of the woods were cut down in the 1970’s and 80’s for road and village/ light industry building construction. Fung shui woods were identified behind the villages of Mong Tseng Tsuen, see Figure 15.8 and Wong Nai Tun Tsuen, see Figure 15.17. None of the villages retained ponds.

 

15.6      Results of the Archaeological Field Evaluation (Construction Phase)

15.6.1   Mong Tseng Tsuen PS (Figure 15.44)

(a) Field scan

Field scan of the area proved difficult, as the Proposed Pumping Station (PPS) area is heavily overgrown. No natural cuts were observed, while the southern end of the PPS was used as dumping area for building rubble.  No archaeological material was found.

 

(b) Minimum of 10 auger hole tests

Ten auger hole tests were evenly spaced within the PPS.  The results of the auger tests indicated that the PPS is an alluvial area with interspersed rocks and water table level at an approximate depth of 1.2 meters below the surface.  No archaeological finds were recovered from the tests.

 

(c) One test pit excavation

The PPS is located on private land and no permission was gained to conduct a test pit excavation. 

 

15.6.2   Sewer alignment on Wang Chau  (Figure 15.43)

(a) Field scan

The surface was scanned for finds wherever possible.  The study area is located on hill slopes and the vegetation cover consists of shrubs and trees.  The hill slopes is occupied by graves and some of the open grave cuts could be checked for finds and stratigraphy.  No archaeological finds were recovered from this area.

 

(b) Minimum of 20 auger hole tests

A total of twenty auger holes were conducted on the lower hill slopes at Wang Chau. The results of the tests indicate colluvial deposits on decomposing rock.  Most of the auger holes had to be abandoned at shallow depths due to rock encounter.  No archaeological finds or cultural soils were encountered in the tests. 

 

(c) Two test pits

Test pit 1(Figure 15.43 and Appendix 15.4)

The test pit was located at the lower hill slopes of Wang Chau in the vicinity of recent graves.  It measured 2 by 2 meters and was hand excavated to a maximum depth of 1.50m.  An auger hole test was conducted to further verify the stratigraphy. 

TBM (0.685m) was taken on a grave located to the south of the test pit. 

 

A total of three sterile contexts were recorded during the excavation (Appendix 15.5).  Context 01 was brown very slightly silty and slightly gravelly silt.  This topsoil had a thickness between 0.12 and 0.24m.  Context 02 consisted of reddish yellow slightly sandy and slightly gravelly silt with angular to sub-angular cobbles.  The colluvial layer had an approximate thickness of 0.70m.  Context 03 was recorded around a depth of 0.80m below the surface and continued until the hand excavation of the test pit was halted for safety reasons at a depth of approximate 1.50m.  It consisted of strong brown slightly sandy and slightly gravelly but very silty clay with decomposing angular to sub-angular cobbles.  The auger hole test was halted immediately below the surface due to rock.

 

Test pit 2 (Figure 15.43 and Appendix 15.4)

The test pit was located at the lower hill slopes of Wang Chau.  It measured 1.5 by 1.5 meters and was hand excavated to a depth of 0.70m due to the encounter of a fairly recent grave.  No auger hole test was conducted due to the grave.

TBM (3.260m) was taken on the grave located to the east-northeast of the test pit.

 

A total of four contexts were recorded during the excavation (Appendix 15.5).  Context 01 was brown very slightly sandy and very slightly clayey silt with angular cobbles and roots.  This topsoil had a thickness between 0.12 and 0.34m.  Context 02 consisted of reddish yellow slightly clayey silt with the occasional angular cobble.  This fill layer contained some concrete chunks and red brick fragments. The fill layer had a thickness between 0.18 and 0.50m and covered the top of a grave structure.  Context 03 is the grave structure itself (Appendix 15.5) and the soil on the western side of the test pit, which had a high lime residue content related to the actual burial coffin (Appendix 15.4).  This soil with lime fragments was encountered at a depth of approximately 0.60m below the surface. Context 04 was light yellowish brown gravelly silt, which was excavated on the front side of the grave, representing the fill/colluvium covering the grave structure.  This layer was excavated to a depth of 0.83m after which the excavation was halted.

 

15.6.3   Sewer alignment north of Tung Tau Tsuen (Figure 15.45)

The following methodology was proposed for the sewer alignment north of Tung Tau Tsuen:

·     Field scan of the entire area

·     Minimum of 20 auger hole tests

·     Two test pits

 

The area however, is covered by asphalt and light industry workshops and was unavailable for testing.

 

15.6.4   Shan Ha Tsuen SPS (Figure 15.46)

(a) Field scan

The PPS area at Shan Ha Tsuen is located between a road and a light industry works area. It is fairly low-lying and small ditches with water run across the site.  The surface of the PPS is mainly covered by grasses and the visibility was relatively good. No archaeological material was found.

 

(b) Minimum of 10 auger hole tests

The PPS area proved more or less rubbish and rubble free. The results of the auger tests indicated that this alluvial area is very wet.  Water table was encountered at depths of 0.50 and 0.60m below the surface in the southern part of the PPS area and approximately 0.90m in other parts.  No archaeological finds were recovered and no cultural soils encountered.

 

(c) One test pit excavation

Test pit 1 (Figure 15.46 and Appendix 15.4)

The test pit was located in the northern part of the PPS.  It measured 2 by 2 meters and was hand excavated to a depth of approximately 0.80m.  An auger hole was conducted to further verify the stratigraphy. 

TBM (0.620m) was taken from the NW corner of the male toilets located to the north west of the test pit.

 

A total of nine contexts were recorded during the excavation (Appendix 15.5).  Context 01 was dark brown very slightly sandy, slightly silty clay.  The topsoil was very irregular in thickness due to the ridge and furrow agriculture and its thickness ranged between 0.08 and 0.20m.  All the subsequent recorded contexts are alluvial deposits.  Context 02 consisted of brown very slightly sandy silty clay and had a thickness between 0.04 and 0.20m.  Context 02 included thirteen tile fragments, fourteen pieces of village ware and four porcelain fragments and one marble (Appendix 15.4).   Context 03 was grey slightly sandy silty clay and had a maximum thickness of 0.12m. This alluvial layer was recorded only in the southern half of the test pit and thinned out towards the north, it included the following material: one small tile fragment and two undiagnostic village ware sherds. Context 04 consisted of yellowish brown slightly sandy and slightly gravelly silty clay with a thickness of 0.15m.  Context 05 was very pale brown slightly silty clay. The hand excavation was halted at depths between 0.38 and 0.78m below the surface due to water table.  Context 05 had a thickness of 0.80m.  Context 06 was found at a depth of 1.20m below the surface and consisted of reddish yellow slightly silty clay.  Context 07 was light brown very slightly clayey sand at a depth of 1.83m below the surface.  Context 08 consisted of grey gravelly sand at a depth of 2.20m below the surface.  And Finally Context 09 was yellowish brown slightly gravelly sand recorded at a depth of 2.25m below the surface. The auger hole test was abandoned at a depth of 2.28m due to auger failing to hold soil.

 

15.6.5   Shung Ching San Tsuen SPS (Figure 15.47)

(a) Field scan

The area of the PPS could be divided into two parts.  The southern half was covered in concrete, which is part of a new residential development called Regalia Garden.  The northern half of the PPS is occupied by high grasses.  The surface wherever possible was scanned for finds, however, the surface was covered by building debris and rubbish in many places.  No archaeological remains were found.

 

(b) Minimum of 10 auger hole tests

All auger tests were positioned in the northern half of the PPS.  The southern half of the PPS was found to be covered in concrete and was not available for testing.  The results of the auger hole tests indicated that the entire area may be covered in fill.  No archaeological findings were recovered from the auger tests.

 

(c) One test pit excavation

Test pit 1(Figure 15.47 and Appendix 15.4)

The test pit was located in the centre of the PPS.  It measured 2 by 2 meters and was hand excavated to a depth of approximately 1.40m.  An auger hole test was conducted to further verify the stratigraphy.

TMB was taken on the south-western corner of the east gate post of the entrance to the Regalia Garden, which is located to the south of the test pit.

 

A total of nine contexts were recorded during the excavation (Appendix 15.5).  Context 01 was light brown very sandy and very gravelly silt with cobbles.  This fill layer also contained building debris, plastic and wood and had a thickness of approximately 0.40m.  Context 02 was a fill layer of brown very gravelly and very sandy silt.  Building debris, metal, plastic, wood and general rubbish was excavated from the Context 02 layer with a thickness between 0.70 and 0.85m.  Context 03 was the last fill layer and consisted of olive sandy and gravelly clay with similar to above inclusions.  It had a thickness of 0.40m.  The hand excavation of the test pit was halted at a depth of approximately 1.40m below the surface.  The auger test recorded the following sterile alluvial contexts: Context 04, very dark grey very slightly sandy silty clay was recorded at a depth of 1.47m below the surface.  Context 05 was olive grey gravelly and silty clay at a depth of 1.58m below the surface.  Context 06 consisted of olive silty and gravelly clay at a depth of 1.70m below the surface.  Context 07 was olive sandy gravel at a depth of 1.92m below the surface. Context 08 consisted of olive yellow very slightly clayey, gravelly sand at a depth of 2.09m below the surface. And finally Context 09 was encountered at a depth of 2.88m below the surface and consisted of light yellowish brown silty, sandy and gravelly clay.  The auger test was halted at a depth of 2.92m below the surface due to end of auger was reached.

 

15.7      Assessment Results for Built Heritage (Construction Phase)

The assessment of impacts will be divided in the following manner:

1) Firstly, by type of resource, i.e. built heritage resources, graves and cultural / historical landscapes;

2) Secondly, by alignment; and

3) Thirdly, by location of the resources and of the works areas,

·     for works areas that are located outside village boundaries, resources within the assessed villages will be grouped as a village group.

·     For works areas that are located within village boundaries, resources in close proximity to the works areas will be assessed individually

·     All resources located outside of village boundaries will be assessed individually

 

The results of the impact assessment will be presented in table form. Tables will be presented for each alignment and will include, the recorded features, their distance from the works and the potential adverse impacts. Both pumping stations and sewage alignments will be assessed as part of the construction phase. The works to be carried out as part of the construction phase are not expected to generate adverse vibration impacts or cause any structural damage to any of the identified resources situated further than 10 metres away from the proposed works. Works to be carried out in very close proximity to identified resources, i.e. > 10 metres may potentially cause contact or vibration damage to these resources. It should be noted that only structures containing historical architectural features will be assessed for vibration damage as part of this report, as heritage resources, such as shrines, ancestral halls etc, that are of modern construction will not require any specialist assessment.

 

15.7.1   Impact on Resources

Lau Fau San to Mong Tseng

Table 15.1:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Alignment or PPS site

 

Potential Negative Impacts

 

San Hing Tsuen

 

 

Tsz Tongs, Houses and a fung shui wall  (AAHB-01 to 20)

 

40m

 

None, as the structures are located at a sufficient distance from the works area

 

Mong Tseng Tsuen

 

 

Tsz Tong, Houses, Well and a Shrine 

(AAHB-29 to 53)

 

15m

 

None, as the structures are located at a sufficient distance from the works area

 

 

 

Chung Yuen

 

Houses and a Shrine

(AAHB-23 to 25)

 

 

40m

 

None, as the structures are located at a sufficient distance from the works area

 

 


Table 15.2:  Potential impacts to resources outside villages

 

Location

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Lau Fau San Road

 

Modern constructed shrine

(AAHB-21)

 

 

Shrine (AAHB-22)

 

 

5m

 

 

 

 

20m

 

 

Possible damage from contact with construction machinery or equipment and possible access restrictions; due to the close proximity to works area.

 

None, as the shrine is located at a sufficient distance from the alignment.

 

Near Sha Kong Wai

 

Temple and Shrine (AAHB-26 and 27)

 

Kwun Yum Statue (AAHB-28)

 

 

30m

 

None, as the temple, shrine and statue are located at a sufficient distance from the alignment.

 

San Tin to Ngau Tam Mei

Table 15.3:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

On Lung Tsuen

 

Various Resources

(AAHB-406 to 418 and 450 to 460)

 

 

20 m

    

    

 

None, as the structures are located at a sufficient distance from the works areas

 

 

Fan Tin Tsuen

 

Various Resources

(420 to 426

and 428 to 432, 484, 485 and 503)

 

 

Ming Yuen Tong (AAHB-433)

 

 

 

 

Shun Yue Tong and San Yeh Man Tong (AAHB-486 and 487)

 

 

 

 

Shrine  (AAHB-419)

 

 

 

 

 

 

Man Lun Fung (AAHB-405)

 

 

 

30 m

  

 

 

 

 

<5 m

 

 

 

 

 

<5 m

 

 

 

 

 

 

<5 m

   

 

 

 

 

 

<5m

 

 

 

None, as the structures are located at a sufficient distance from the works areas

 

 

 

 

Possible structural damage from vibration and/or contact with construction machinery or equipment due to the close proximity to works area.

 

 

Possible structural damage from vibration and/or contact with construction machinery or equipment due to the close proximity to works area.

 

 

 

Possible structural damage from vibration and/or contact with construction machinery or equipment and possible access restrictions; due to the close proximity to works area.

 

 

Possible structural damage from vibration and/or contact with construction machinery or equipment due to the close proximity to works area.

 

 

San Lung Tsuen

 

Various Resources (AAHB-436, 481, 482, 488 to 494 and 496 to 502)

 

 

10 m

 

 

 

 

None, as the structures are separated from the works area by modern buildings.

 

Mai Po Tsuen

 

Well, Village Gate, Ancestral Hall, House, Shrine and Temple

(AAHB- 229 to 241)

 

15 m

 

None, as the structures are located at a sufficient distance from the alignment and separated from it by a concrete wall.

 

 

 

Table 15.4:  Potential impacts to resources outside villages

 

 

Location

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Castle Peak Road (San Tin to Mai Po)

 

 

Temple (AAHB-505)

 

 

Temple

 

and shrine

 (AAHB-227)

 

 

 

 

 

Well (AAHB-228)

 

 

Modern village Gates (AAHB-231 and 240)

 

100 m

 

 

>5 m

 

 

 

 

 

 

 

 

20 m

 

 

>5 m

 

 

 

None, as the temple is located at a sufficient distance from the alignment.

 

Possible structural damage to the temple from vibration and/or contact with construction machinery or equipment and possible access restrictions to both the temple and shrine; due to the close proximity to works area and works area being located on the access route.

 

 

None, as the well is located at a sufficient distance from the works areas

 

Possible damage from contact with construction machinery or equipment.

 

 

Castle Peak Road (Yau Mei Tsuen)

 

Shrine (AAHB-242)

 

 

 

Gate (AAHB-243)

 

30 m

 

 

 

25 m

 

Access restrictions, as the path to the shrine originates on Castle Peak Road (a works area)

 

None, as the gate is located at a sufficient distance from the alignment.

 

Shap Pat Heung

 

(a) Shan Ha Tsuen

Table 15.5:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Shan Ha Tsuen

 

Houses, Stone Platform, Tsz Tongs/ Study halls, Well, Cannons and a Shrine

(AAHB-177 to 206)

 

 

30 m

 

 

 

 

 

None, as the structures are located at a sufficient distance from the alignment and the proposed pumping station is not visible from any of the recorded resources.

 

 

(b) Kung Um Road

Table 15.6:  Potential impacts to resources within villages

 

Location

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Tin Liu Tsuen

 

Shrine, Houses, Temple and a Well

 (AAHB-244 to 260)

 

 

20 m

 

 

 

None, as the structures are located at a sufficient distance from the works area

 

Muk Kiu Tau Tsuen

 

Modern constructed shrine (AAHB-262)

 

 

 

Gate, Well, Houses, Ancestral Hall and Temple

 (AAHB-261 and 263 to 271)

 

 

<5  m

 

 

 

 

100 m

 

 

 

Possible damage from contact with construction machinery or equipment and possible access restrictions; due to the close proximity to works area.

 

None, as the structures are located at a sufficient distance from the works areas

 

Pak Sha Tsuen

 

Shrine (AAHB-272)

 

 

Gate Houses Temple Shed Study hall  and Well

 (AAHB-273 to 284)

 

 

10 m

 

 

60 m

 

 

 

 

None, as the structures are located at a sufficient distance from the works areas

 

 

(c) Sham Chung Drainage Alignment

Table 15.7:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Tai Tong Tsuen

 

 

Gate, Shrines, Ancestral halls, Shed, Study Hall and houses  (AAHB-54 to 69)

 

 

35 m

 

 

 

 

None, as the structures are located at a sufficient distance from works areas

 

 

Wong Nai Tun Tsuen

 

Shrine, Tsz Tong and

Houses

(AAHB-70 to 86)

 

 

50 m

 

 

 

None, as the structures are located at a sufficient distance from the works area

 

 

Shui Tsiu San Tsuen

 

Study Halls, Houses, Ancestral halls, Gates and Shrines  (AAHB-87 to 116)

 

 

50 m

 

 

 

 

 

None, as the structures are located at a sufficient distance from the works area

 

 

Sham Chung Tsuen

 

Houses, Temple and Shrine

 (AAHB-117 to 128)

 

 

90 m

 

 

 

 

None, as the structures are located at a sufficient distance from the alignment

 

 

 

Table 15.8:  Potential impacts to resources outside villages

 

Location

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

 Near Tai Tong

 

 

School (AAHB-86)

 

 

20 m

 

 

None, as the school grounds are separated from the works area by a compound wall and the alignment is located within the bounds of a large drainage channel.

 

 

Near Sham Chung Tsuen

 

 

Shrine (AAHB-130)

 

10 m

 

None, as the structures are located at a sufficient distance from the alignment

 

(d) Tai Tong Road

Table 15.9:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Shui Tsui Lo Wai

 

Houses, Ancestral halls, Shrine, Study hall and cannon (AAHB-131 to 153)

 

 

50 m

 

 

 

 

None, as the structures are located at a sufficient distance from the alignment

 

 

Hung Tso Tin

 

Well, Ancestral hall, House  (AAHB-154 to 162)

 

 

30 m

 

 

 

None, as the structures are located at a sufficient distance from the alignment

 

 

Nam Hang Tsuen

 

Houses and Temple (AAHB-165, 166, 167 to 173)

 

 

70 m

 

 

 

None, as the structures are located at a sufficient distance from the alignment

 

 

Cheng Chu Wai

 

Gate, Well, House (AAHB--174 to 176)

 

30 m

 

 

None, as the structures are located at a sufficient distance from the alignment

 

Table 15.10:  Potential impacts to resources outside villages

 

Location

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Tai Tong Road

 

Modern constructed village gates (AAHB-129, 131, 162, 153, 164 and 211)

 

Temple (AAHB-163)

 

 

School (AAHB-215)

 

 

Shrine (AAHB-207)

 

 

House (AAHB-208, 209 and 210)

 

Inscription stone (AAHB-212)

 

 

5 m

 

 

 

 

30 m

 

 

20 m

 

 

>5 m

 

 

55 m

 

 

10 m

 

 

 

Possible damage from contact with construction machinery or equipment and possible access restrictions; due to the close proximity to works area.

 

None, as the structures are located at a sufficient distance from the alignment

 

None, as the structures are located at a sufficient distance from the alignment

 

Possible contact damage and access restrictions due to the close proximity to works areas

 

None, as the structures are located at a sufficient distance from the alignment

 

None, as the inscription stone is located at a sufficient distance from the alignment.

 

 

(e) Tai Shu Ha Road

Table 15.11:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Tong Tau Po Tsuen

 

Gates, Ancestral Hall and Houses

 (AAHB-217 to 233)

 

 

70 m

 

 

 

 

None, as the structures are located at a sufficient distance from the alignment.

 

Table 15.12:  Potential impacts to resources outside villages

 

Location

 

 

Resource

 

Minimum Distance to the Alignment or PPS Site

 

Potential Negative Impacts

 

Tai Shu Ha Road East

 

Shrine (AAHB-224)

 

 

 

 

House (AAHB-225)

 

 

 

Temple (AAHB-226)

 

>5 m

 

 

 

 

80 m

 

 

 

20 m

 

Possible damage from contact with construction machinery or equipment and possible access restrictions; due to the close proximity to works area.

 

None, as the house is located at a sufficient distance from the alignment.

 

 

Access restrictions from works on Tai Shu Ha Road East

 

 

Tai Shu Ha Road West

 

(Shung Ching Tsuen)

 

House (AAHB-213)

 

Church (AAHB-214)

 

Ancestral Hall (AAHB-216)

 

60 m

 

90 m

 

70 m

 

None, as the structures are located at a sufficient distance from the alignment

 

Yuen Long Effluent Pipeline

Table 15.13:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Alignment

 

Potential Negative Impacts

 

Shing Uk Tsuen

 

House, Tsz Tong, Study Hall and Shrine (AAHB-285 to 314)

 

 

40 m

 

 

 

 

None, as the structures are located at a sufficient distance from the alignment.

 

 

Tai Tseng Wai

 

House, Gate, Tsz Tong, Study Hall and Shrine (AAHB-315 to 354)

 

 

40 m

 

None, as the structures are located at a sufficient distance from the alignment.

 

 

Ng Uk Tsuen

 

House, Sheds, Shrine, Tsz Tong, Well, Gate, School and Rural Committee Building (AAHB-356 and 358 to 393)

 

55 m

 

 

 

None, as the structures are located at a sufficient distance from the alignment.

 

 

Table 15.14:  Potential impacts to resources outside villages

 

Location

 

Resource

 

 

Minimum Distance to the Alignment

 

Potential Negative Impacts

 

Near Ng Uk Tsuen

 

Temple

(AAHB-355)

 

85 m

 

None, as the temple is located at a sufficient distance from the alignment

 

 

Corner of Fuk Shun St. and WSD service Road

 

Shrine

(AAHB-357)

 

<5m

 

Possible damage from contact with construction machinery or equipment and possible access restrictions; due to the close proximity to works area.

 

 

15.7.2   Impact on Buddhist Blessing Stones

All of the Buddhist blessing stones are located within close proximity to the works areas and may receive possible contact damage due to their close proximity to works areas.

 

15.7.3   Impact on Graves

The following assessment is based on the following factors, the type of works associated with the proposed project, the distance of the works and the fact that all of the graves are modern reconstructions, consisting of, in almost all cases, concrete. These graves do not possess historical architectural features that would possibly require special protective measures due to their fragile nature, during construction. 

 

Table 15.15:  Impacts to recorded graves

Number

Location

Distance from alignment

Potential Negative Impact

YLKT-G1

Mong Tseng Tsuen

60 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G2

Mong Tseng Tsuen

100metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G03

Mong Tseng Tsuen

50 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G04

San Tin Park

60 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G05

Ka Lung Road

20 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G06

Ka Lung Road

20 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G07

Ka Lung Road

30 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G08

Ka Lung Road

25 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G09

Ka Lung Road

25 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G10

Ka Lung Road

25 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G11

Ka Lung Road

25 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G12

Ka Lung Road

25 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G13

Ka Lung Road

15 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G14

Ka Lung Road

50 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G15

Ka Lung Road

50 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G16 (A to F)

Ka Lung Road

50 metres

None, as the grave is located at a sufficient distance from the alignment

YLKT-G17

Ka Lung Road

10 metres

None, as the grave is located at a sufficient distance from the alignment

 

15.7.4   Impact on Cultural and Historical Landscape Features

The two identified features, i.e. the fung shui woods associated with the villages of Mong Tseng Tsuen and Wong Nai Tun Tsuen both lie at a sufficient distance from the works area and will not be impact by the proposed projects.

 

15.8      Assessment Results on Archaeology (Construction Phase)

15.8.1   Desk-based assessment result (Archaeology During Construction Phase)

 

The results of the desk-based research identified:

·     Areas of archaeological potential, of which five areas were agreed with the AMO for field evaluation at the EIA stage (field evaluation results are presented below);

·     Yuen Long sewage treatment works effluent pipeline, conforming scheme 2A-IT is not the preferred option and has not been assessed, if this alignment is the preferred option and full cultural heritage impact assessment will have to be conducted; and

·     Area of archaeological potential currently under road and thus not accessible for field evaluation :

 

Sewer alignment from YLEPS to Wang Chau

This proposed sewer alignment will occur on both Pleistocene terraced alluvium and debris flow deposits.   The existing impacts on these original landforms, according to the desk-based research, are limited to water mains alignment and PCCW cable on the road. The area between the villages lies at a PD level of approximately 5m. Archaeological sites are known on similar landform as described here, for instance at Mong Tseng, Mai Po, Tung Tau and Tseung Kong Wai.  The desk-based research did not indicate disturbance of the area along the road and identified no previous investigation in the area. 

 

15.8.2   Assessment of the field evaluation (Archaeology during Construction Phase) – Appendix 15.6

(a) Mong Tseng Tsuen PS

Auger test results indicate an alluvial deposit is located at the PPS area.  The proximity of the historical buildings of Mong Tseng suggests Qing Dynasty material should be found, although none was recovered from the auger hole testing.  A test pit excavation will confirm any Qing Dynasty remains or identify other periods in this area. 

 

(b) Sewer alignment on Wang Chau

The field scan, auger programme and test pit excavations all identified that the lower hill slopes of Wang Chau have no archaeological potential.

 

(c) Sewer alignment north of Tung Tau Tsuen

The desk-based research had identified the sewer alignment at Tung Tau Tsuen to have archaeological potential, due to asphalt and concrete cover the area proved not available for testing at this moment. 

 

(d) Shan Ha Tsuen SPS

Auger test and test pit excavation results indicate an alluvial deposit is located at the PPS area.  The deposits were sterile and the water table level was encountered at depths above 1 meter below the surface. No archaeological deposits, features or cultural soils were encountered.

 

(e) Shung Ching San Tsuen SPS

Part of the area was unavailable for testing.  The portion, which was tested during the field evaluation, indicated that the area has been artificially raised.  Original alluvial layers did not appear until 1.55m below the surface. The alluvial deposits are low-lying and near water table, diminishing the archaeological potential in this area.

 

15.9      Mitigation Measures on Built Heritage for Construction Phase

The presentation of mitigation measures will be presented in the following tables.

 

Lau Fau Shan to Mong Tseng Tsuen

 

Table 15.16:  Mitigation recommendations for resources within villages

Location

Resource

Distance

Mitigation Recommendations

 

Lau Fau Shan Road

 

Modern constructed shrine (AAHB-21)

 

 

 

 

 

 

>5 m

 

 

 

 

 

 

 

The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing; 

 

Access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

 


San Tin to Ngau Tam Mei

Table 15.17:  Mitigation recommendations for resources within villages

Location

Resource

Distance

Mitigation Recommendations

 

Fan Tin Tsuen

 

Man Lung Fung Ancestral Hall (AAHB-405)

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Shrine (AAHB-419)

 

 

 

 

 

 

Ming Yuen Tong (AAHB-433)

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Shun Yue Tong and San Yeh Man Tong (AAHB-486 and 487)

 

 

 

<5m 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

<5 m

 

 

 

 

 

 

<5 m 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

<5m

 

 

 

As the works are in close proximity to the southwestern wall of the ancestral hall, which is a Declared Monument, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended.

 

The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing; 

 

Access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

As the works are in close proximity to the southeastern wall of the ancestral hall, which is a Grade II building, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended.

 

The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

As the works are in close proximity to the southeastern walls of both of the Shun Yue Tong and San Yeh Man Tong, which are Grade I and Grade II buildings, respectively, the contractor must carry out a condition survey of both of the buildings. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended.

 

The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

 

 


Table 15.18:  Mitigation recommendations for resources outside villages

Location

Resource

Distance

Mitigation Recommendations

 

Castle Peak Road (San Tin to Mai Po)

 

Temple

 

and shrine

 

(AAHB-227)

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Modern constructed village gates

(AAHB-231 and 240)

 

>5 m

 

10m

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

>5 m

 

The temple, although renovated contains historical architectural elements and is located directly on the edge of the works area. Hence, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended. The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

The shrine is located at a sufficient distance as to not require any protective measures during the construction phase. Access to the temple and shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

The base of the gates should be provided with a protective covering in the form of heavy duty plastic sheeting, supported by scaffolding where necessary.

 

 

Castle Peak Road (Yau Mei Tsuen)

 

Shrine (YLKT-02-242)

 

30 m

 

The shrine is located at a sufficient distance as to not require any protective measures during the construction phase. Access from Castle Peak Road should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

 

Shap Pat Heung

(a)Shan Ha Tsuen

There were no impacts associated with this alignment and pumping station, therefore no mitigation is required.

 

(b) Kung Um Road

Table 15.19:  Mitigation recommendations for resources within villages

Location

Resource

Distance

Mitigation Recommendations

 

Muk Kiu Tau Tsuen

 

Shrine (AAHB-262)

 

 

 

5 m

 

The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing; 

 

Access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

 

(c) Sham Chung Drainage Channel

 

There were no impacts associated with this alignment and pumping station, therefore no mitigation is required.

 

 


(d) Tai Tong Road (Northern Section)

Table 15.20:  Mitigation recommendations for resources outside villages

Location

Resource

Distance

Mitigation Recommendations

 

Tai Tong Road

 

Gates

(AAHB-129,131,153,162, 164 and 211)

 

 

c.5 m

 

The base of the gates should be provided with a protective covering in the form of heavy duty plastic sheeting, supported by scaffolding where necessary.

 

Tai Tong Road

 

Shrine (AAHB-207)

 

>5 m

 

The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing; 

 

Access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

 

(e) Tai Shu Ha Road

Table 15.21:  Mitigation recommendations for resources outside villages

Location

Resource

Distance

Mitigation Recommendations

 

Tai Shu Ha Road East

 

Shrine (AAHB-224)

 

 

 

 

 

 

 

 

Temple (AAHB-226)

 

 

>5 m

 

 

 

 

 

 

 

 

15 m

 

The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing; 

 

Access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

 

The entrance to the temple is located directly from Tai Shu Ha Road, access from the road should be maintained throughout the construction phase.

 

 

(f) Tai Shu Ha Road West

There were no impacts associated with this alignment and pumping station, therefore no mitigation is required.

 

 

Yuen Long Effluent Pipeline

Table 15.22:  Mitigation recommendations for resources outside villages

Location

Resource

Distance

Mitigation Recommendations

 

Corner of Fuk Shun St. and WSD Service Road

 

Shrine

(AAHB-357)

 

<5m

 

The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing; 

 

Access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

 

15.9.1   Buddhist Blessing Stones

The stones do not contain any fragile elements and will not require any protective measures during the works.

 

15.9.2   Graves

There will be no impacts to any of the surveyed graves in the study area or to those located within the Cassino camp, therefore no mitigation measures will be necessary.

 

15.9.3   Cultural and Historical Landscape Features

No cultural or historical landscape features will be impacted by the project, therefore, no mitigation measures will be required.

 

15.10    Mitigation Measures on Archaeology for Construction Phase

15.10.1Mong Tseng Tsuen PS (non-designated element)

The site is private and field survey was not allowed.  Further investigation should be carried out after the resumption of the land and prior to commencement of any works.  The investigation should comprise of a minimum of one test pit excavation, measuring no less than 2 by 2 meters to verify the stratigraphy and potential archaeological deposits in the Mong Tseng PPS.

 

15.10.2Sewer alignment on Wang Chau (non- designated element)

The results from the field investigation indicate a lack of archaeological deposits and cultural soils.  No further action is required.

 

15.10.3Sewer alignment north of Tung Tau Tsuen (non- designated element)

The site was occupied by local villagers and field survey was not allowed.  Investigation should be carried out after the resumption of the land and prior to commencement of any works.  The investigation should comprise of a minimum of 20 auger hole tests and two test pit excavations measuring no less than 2 by 2 meters to verify the stratigraphy and potential archaeological deposits within the known archaeological site. 

 

15.10.4Shan Ha Tsuen SPS (non-designated element)

The field investigation results indicate that the area exists of sterile alluvial deposits with a high water table and is thus considered to have no archaeological potential.  No further action is required.

 

15.10.5Shung Ching San Tsuen SPS (non-designated element)

The field investigation results indicate that the area has been artificially raised by 1.5m fill.  Sterile alluvial deposits were encountered at a depth of more than 1.5m. No further action is required.

 

15.10.6Sewer alignment from YLEPS to Wang Chau (non- designated element)

Archaeological monitoring is recommended during the excavations of the sewer alignment between the historic villages of Tai Tseng Ng Uk Tsuen, Tai Tseng Wai and Shing Uk Tsuen. 

 

15.11    Assessment Methodology for Operational Phase

15.11.1Potential Sources of Impact During Operational Phase

Archaeology.

No impacts on archaeological deposits are anticipated during the operational phase.

 

Built Heritage

The impact assessment for the operational phase will deal with the proposed sites of the pumping stations and will entail aesthetic impacts. The recording methodology used in the assessment will be the same as that used for the construction phase.

 

15.11.2Assessment Approach for Operational Phase

The assessment methodology for impacts, which may occur during the operational phase is the same as for impacts which will occur during the construction phase.

 

15.12    Assessment Results for Operational Phase

15.12.1Archaeology

The impacts on the archaeological deposits will occur during the construction phase.  No impacts are expected during the operational phase.

 

15.12.2Built Heritage

The impacts with the operational phase are associated with the proposed pumping station buildings.

 

Lau Fau Shan to Mong Tseng Tsuen

(a) Mong Tseng Tsuen pumping Station

 

Table 15.23:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Proposed Pumping Station

 

Potential Negative Impacts

 

Mong Tseng Tsuen

 

 

Tsz Tong, Houses, Well and Shrine (AAHB-29 to 53)

 

 

15 m

 

Aesthetic impacts affecting the environmental setting of the resources

 

San Tin to Ngau Tam Mei

Table 15.24:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Proposed Pumping Station

 

Potential Negative Impacts

 

On Lung Tsuen

 

Various resources

(AAHB-406 to 418 and 450 to 460)

 

 

60 m

 

 

 

 

None, as the structures are not located in the vicinity of a proposed pumping station

 

 

Fan Tin Tsuen

 

Various Resources (AAHB-419 to 426, 428 to 432, 484, 485 and 503)

 

 

Man Lun Fung (AAHB-405)

 

Ming Yuen Tong (AAHB-433)

 

 

40 m

 

 

 

 

 

10 m

 

 

15 m

 

 

None, as the structures are not located in the vicinity of a pumping station

 

 

 

 

 Aesthetic impacts affecting the environmental setting of the resources

 

San Lung Tsuen

 

Various Resources (AAHB-436, 481, 482, 488 to 494 and 496 to 502)

 

 

45 m

 

 

 

 

None, as the structures are not located in the vicinity of a pumping station

 

 

 

Table 15.25:  Potential impacts to resources outside villages

 

Location

 

 

Resource

 

Minimum Distance to the Proposed Pumping Station

 

Potential Negative Impacts

 

Castle Peak Road (San Tin to Mai Po)

 

 

Temple (AAHB-505)

 

Temple and shrine (AAHB-227)

 

Well (AAHB-228)

 

Gates (AAHB-311 and 321)

 

over 100 m

 

over 100 m

 

 

over 100 m

 

over 100 m

 

 

 

 

None, as the structures are not located in the vicinity of a pumping station

 

 

 

 

Castle Peak Road (Yau Mei Tsuen)

 

Shrine (AAHB-242)

 

Gate (AAHB-243)

 

over 100 m

 

over 100 m

 

None, as the structures are not located in the vicinity of a pumping station

 

 


Shap Pat Heung

(a) Shan Ha Tsuen

Table 15.26:  Potential impacts to resources within villages

 

Village

 

 

Resource

 

Minimum Distance to the Proposed Pumping Station

 

Potential Negative Impacts

 

Shan Ha Tsuen

 

Houses, Stone Platform, Tsz Tongs/ Study halls, Well, Cannons and a Shrine

(AAHB-177 to 206)

 

30 m

 

 

 

 

None, as the structures are not located within the vicinity of a pumping station.

 

(b) Kung Um Road

Table 15.27:  Potential impacts to resources within villages

 

Location

 

 

Resource

 

Minimum Distance to the Proposed Pumping Station

 

Potential Negative Impacts

 

Pak Sha Tsuen

 

Gate Houses Temple Shed Study hall and Well and Shrine

 (AAHB-272 to 284)

 

 

60 m

 

 

 

 

None, as the structures are not located in the vicinity of a pumping station

 

 

(c) Sham Chung Drainage Channel

There are no resources within 100 metres of a proposed pumping station; therefore, there will be no associated impacts.

 

(d) Tai Tong Road (Northern Section)

There are no resources within 100 metres of a proposed pumping station; therefore, there will be no associated impacts.

 

(e) Tai Shu Ha Road

Table 15.28:  Potential impacts to resources outside villages

 

Location

 

 

Resource

 

Minimum Distance to the Proposed Pumping Station

 

Potential Negative Impacts

 

Tai Shu Ha Road East

 

Temple (AAHB-226)

 

20 m

 

Aesthetic impacts affecting the environmental setting of the resources

 

 

Yuen Long Effluent Pipeline

There are no resources within 100 metres of a proposed pumping station, therefore, there will be no associated impacts.

 

15.13    Mitigation Measures for Operational Phase

15.13.1Archaeology

No mitigation measures are required as no impacts are expected during the operational phase.

 

15.13.2Built Heritage

Built Features

The following resources will require mitigation measures with respect to the operational phase. The Mong Tseng Tsuen, Fan Tin Tsuen and Nga Yiu Tau pumping stations are non-Designated Elements.

 

(a) Lau Fau Shan to Mong Tseng

Table 15.29:  Mitigation recommendations for resources within villages

Location

Resource

Minimum Distance to PPS Site

Mitigation Recommendations

 

Mong Tseng Tsuen

 

Village structures (AAHB-29 to 53)

 

15 m

 

 

As the pumping station is located at the front of the village, the landscaping of the area around the pumping station should include planting of foliage complimentary to the existing environmental setting, in order to screen the proposed pumping station and minimise visual impacts.

 

The colour treatment of the proposed pumping station should minimise visual impact.

 

(General examples can be found in Figures 14.62 through 14.65)

 

 

(b) San Tin to Ngau Mei Tsuen

Table 15.30:  Mitigation recommendations for resources within villages

Location

Resource

Minimum Distance to PPS Site

Mitigation Recommendations

 

Fan Tin Tsuen

 

Man Lung Fung Ancestral Hall (AAHB-405)

 

 

 

Ming Yuen Tong (AAHB-433)

 

 

 

 

10 m

     

 

 

 

 

15 m

    

 

 

 

 As the proposed pumping station is located in the vicinity of two Tsz Tongs, one of which is a Declared Monument, the landscaping of the area around the proposed pumping station should include planting of foliage complimentary to the existing environmental setting, in order to screen the proposed pumping station and minimise visual impacts.

 

The colour treatment of the proposed pumping station should minimise visual impact. Itis recommended that the design and materials of the proposed pumpingstation should visually harmonize with the existing historic ancestralhalls of Man Lun Fung and Ming Yuen Tong, for example, grey brickwork andgranite are preferable for the exterior elevations.

 

(General examples can be found in Figures 14.62 through 14.65)

 

 

(c) Tai Shu Ha Road

Table 15.31:  Mitigation recommendations for resources outside villages

Location

Resource

Distance

Mitigation Recommendations

 

Tai Shu Ha Road East (Nga Yiu Tau)

 

Temple (AAHB-226)

 

 

20 m

 

The landscaping of the area around the pumping station should include planting of foliage complimentary to the existing environmental setting, in order to screen the proposed pumping station and minimise visual impacts.

 

The colour treatment of the proposed pumping station should minimise visual impact.

 

(General examples can be found in Figures 14.62 through 14.65)

 

 

Buddhist Blessing Stones

Buddhist blessing stones are placed at roadsides and mark the location of a fatal accident. The surrounding environment is not a relevant factor and thus they do not need to be assessed as to changes in their environmental setting.  

 

Graves

There will be no impacts to any of the surveyed graves in the study area or to those located within the Cassino camp, therefore no mitigation measures will be necessary.

 

Cultural and Historical Landscape Features

No cultural or historical landscape features will be impacted by the project, therefore, no mitigation measures will be required.

 


16.0      Fishery impact

This Section of the EIA Report presents the findings of the impact assessment of the construction and operation of the proposed sewerage system and pumping stations on aquaculture fisheries resources and operations.  Baseline information on the potentially affected existing aquaculture fisheries resources and operations is presented and evaluated. 

 

16.1      Legislation and Standards

The criteria for evaluating fisheries impacts are laid out in the Technical Memorandum on Environmental Impact Assessment Process (EIAO-TM).  Annex 17 of the EIAO-TM outlines the general approach and methodology for the assessment of impacts.  Annex 9 of the EIAO-TM recommends some general criteria that can be used for evaluating impacts to fisheries, including aquaculture fisheries resources and operations.

 

Other relevant environmental references, legislation, guidelines and include:

* Relevant Study Brief;

* Hong Kong Planning Standards and Guidelines (HKPSG) Chapter 10;

* Fisheries Protection Ordinance (Cap. 171) 1987 and its subsidiary legislation, the Fisheries Protection Regulations.

 

Fisheries Protection Ordinance (Cap. 171) provides for the conservation of fish and other aquatic life and regulates fishing practices.

 

16.2      Assessment Methodology

The requirements of fisheries impact assessment of the Project area followed Section 3.4.7, Appendix 3 of the Study Brief. The study brief indicated the criteria and guidelines for assessing fisheries impacts as specified in Annexes 9 and 17 of the EIAO TM should be followed.

 

For the purpose of fisheries assessment, the assessment area is defined as all areas within 500m from the site boundary of the works area. This definition meets the requirement as stipulated by the Study Brief, i.e. “the assessment area for fisheries impact assessment included but was not limited to the fishponds in the Conservation Area near Shan Pui River and any other water system identified for fisheries purpose during the course of study”.

 

A desktop review of baseline conditions was conducted using relevant literature, aerial photographs and a Geographical Information System (GIS).  A number of more focused baseline field surveys were then proposed to supplement and verify the review findings. 

 

A literature review was undertaken to describe the baseline conditions in the Assessment Area, and to identify areas and species of potential fisheries importance which may be affected by the project. Reviewed documents include Government and private sector reports, as well as unpublished information.

 

The commercial fishery in Hong Kong is composed of capture fisheries and culture fisheries. The AFCD annual reports from 1991/1992 to 1999/2000 were consulted to assess pond culture fisheries impacts.

 

Field verification of the operational status of the fishponds in the Assessment Area were conducted at intervals during June 2002 and January 2003 simultaneously with the habitat surveys for terrestrial ecology. Fisheries operations such as stocking, feeding and harvesting, the presence of fisheries devices such as aerators and anti-cormorant wires, and the maintenance conditions of the facilities along the pond bunds were noted. The status of fishponds (active or abandoned) was evaluated based upon management conditions of the ponds, the presence of fish farming materials and/or equipment, and fish farming activities. The information presented in the following sections has been based on the findings of the review and these surveys.

 

16.3      Fisheries Baseline Condition

As stipulated in Section 3.4.7 of the EIA Study Brief, within the "Assessment Area", special attention should be paid to the fishponds in the Conservation Area near Shan Pui River.

 

Inland fishponds in Hong Kong, covering 1060 ha in 2000, are mainly located in the northwest New Territories. 2820 tonnes of freshwater fish, including mostly Chinese carp and some tilapia, grey mullet, snakehead and catfish, were produced in 2000, accounting for 6% of the local freshwater fish consumption.

 

Fishponds in the Deep Bay area and the northwest New Territories probably peaked in area during the 1970s or 1980s. In recent years, these ponds have been increasingly subject to conversion for other, more lucrative landuses, including open storage. Development projects including roads, railways, flood control schemes and housing developments have also accounted for a certain amount of pond loss.

 

Figure 13.2 of Section 13 shows the distributions and status of fishponds in the Assessment Area for the proposed project. Within this area, there are about 113 fishponds covering 295 ha. Among them, 60 fishponds are active (covering 230 ha), while the remaining 53 are abandoned (covering 65 ha).

 

The majority of the Study Area to be affected by the proposed Project has been degraded by development and urbanisation. Fisheries sensitive receivers in the Study Area comprise active fishponds. 

 

Results from the survey estimated that there are approximately one hundred and thirteen fishponds in this area.  It is estimated that the fishponds make up an area of approximately 295 hectares. The majority (78% of the total, equivalent to about 230 hectares) of these fishponds are active.  The active fishponds concentrate in Shan Pui (to the north of Yuen Long Industry Estate), along the both sides of the shores of Channel 60CD (Nam Sang Wai & Tai Sang Wai), Mai Po Lo Wai and San Tin. The predominant fish species cultured in these ponds include the mullet (Mugil cephalus) and the four carp species traditionally cultured in Chinese pond aquaculture.  These are the grass carp (Ctenopharyngodon idellus), the silver carp (Hypophthalmichthys molitrix), big-head carp (Aristichthys nobilis) and the common carp (Cyprinus carpio). Snakehead and catfish are also cultured.

 

The remaining active fishponds and all abandoned fishponds are scattered within the Assessment Area among urbanised/disturbed habitats. Apparently not all ponds were managed, i.e. no pump was seen and most grassy bunds were not trimmed. . Most of the ponds still had open water, except one that was overgrown with vegetation.

 

Fishponds at San Wai were ranked as Grade C by the Agriculture, & Fisheries & Conservation Department (AFD undated). The Categorization of Agricultural Land of AFCD ranking recorded 13 ha of fishponds at Hung Shui Kiu - Ha Tsuen area in 1995 (Reference No. 49, covering Fung Kong Tsuen, Tseung Kong Tsuen, Sik Kong Tsuen, Tung Tau Tsuen, Lo Uk Tsuen, San Wai, San Sang Tsuen, Lee Uk Tsuen and Shek Po Tsuen, see AFD 1995) and all agricultural lands were ranked as Grade D (AFD 1995) [30]. The AFCD categorization stated that most agricultural land in the area has been converted for use as open storage (ibid.) [30]. The field survey of the present project verified and confirmed the ranking and description in 1995.

 

34 ha of fishponds were recorded at the area from Lau Fau Shan to Tsim Bei Tsui in 1995 by AFCD (Reference No. 21, covering Sha Kiu Tsuen, Mong Tsang Wai, San Hing Tsuen, Sha Kong Wai and Lau Fau Shan, see AFD 1995). Though the agriculture lands there were ranked as Grade B (ibid) [30] but the fishponds themselves were ranked as the lowest grade for fishponds (Grade C: Areas with scattered small fishponds and substantial amount of fishponds are either either idle or filled. They are subject to high development pressure due to its proximity to developments) (AFD undated) [31].

 

505 ha of fishponds were recorded in the area from Ng Uk Tsuen North, Shan Pui North to Nam Sang Wai and Tai Sang Wai (Reference No.9, see AFD 1995) [30]. Both the agricultural lands inside this area and the fishponds themselves were ranked as Grade A.

 

In the area from Chuk Yuen Tsuen to Lok Ma Chau, 395 ha of fishponds were recorded in 1995 (Reference No.10, covering Chuk Yuen, Tai Shang Wai, Mai Po North, Lo Wai, Sna Tin North, Tam Kon Chau and Lok Ma Chau West, see AFD 1995). Both the agricultural lands inside this area and the fishponds themselves were ranked as Grade A.

 

All fishponds in the Shap Pat Heung area were ranked as Grade C. Only 11 ha of fishponds were recorded within the entire area (Reference 32, 42 & 43) in 1995 (AFD 1995) [30].

 

In the present study, only 0.75ha of active fishponds were recorded within the part of the assessment area which covers Shap Pat Heung, while 116.72 ha of active and 30.96 ha of abandoned fishponds were recorded within the part of the assessment area which covers Ngau Tam Mei and San Tin Areas (2A-2T and 2B-1T).  112.5 ha of active and 33.62 ha of abandoned fishponds were left in the remaining assessment area.

 

Table 16.1:  Areas of fishponds within the 500m study area

 

Area (ha)

Works Package

Active Fishponds

Abandoned Fishponds

Ngau Tam Mei and San Tin Areas (2A-2T and 2B-1T)

116.72

30.96

Lau Fau Shan and Mong Tseng Areas (2A-3T)

Tin Shui Wai and San Wai Areas (Alternative 2A-1T)

112.50

33.62

Shap Pat Heung Area (2B-2T)

0.75

0

 

Based upon the above review of baseline fisheries conditions in the Assessment Area, the sensitive fisheries receivers which may be affected by the proposed project have been identified as the active fishponds within the assessment area.

 

16.4      Impact Identification and Evaluation for Construction Phase

Impact assessment methodology follows the criteria and guidelines for evaluating and assessing fisheries impact as stated in Annex 9 and 17 of the EIAO-TM.  Impacts are generally ranked as "minor", "moderate" or "severe", although in a few cases a ranking of "minimal" (less than "minor") may be given. The ranking of a given impact will vary based on the criteria in the EIAO-TM. The major factors giving rise to a ranking are explained in the text.

 

The fisheries impacts of the project components are assessed individually, then cumulatively with other past, ongoing and proposed projects. Where negative impacts are identified, efforts are made to identify feasible mitigation measures which might be developed to reduce the severity of negative impacts. These measures should be described in terms of their scope, programme, feasibility and financial implications during the construction and operation of the project. Finally, the consultants determined whether the proposed mitigation measures, if implemented, could bring the negative impacts of the project and its components within acceptable bounds.

 

Predominant impacts to fishery operations and resources usually occur through the loss, temporary or permanent, of areas supporting fisheries resources.

 

In the present proposed project, however, there will be no marine or intertidal infrastructure element involved. No temporary or permanent loss of fishing grounds or mariculture sites would result from implementation of the project. Indirect impacts on marine capture and culture fisheries usually are usually caused by changes in marine water quality. As no marine or intertidal construction works are involved, and the surface runoff will be minimal due to the distance from the construction sites to the coastline, there will be no indirect impacts to marine capture and marine culture fisheries during the construction phase. Therefore no impacts from construction of the present project on marine capture and culture fisheries are anticipated.

 

The potential impacts to aquaculture fisheries resources and operations arising from the construction of the proposed sewerage system and pumping stations include the direct loss of fishpond habitat resulting from the construction of the Project.

 

For inland fishponds, only a part (0.05 ha) of one fishpond on the alignment of sewer from the existing San Wai STW toward Tin Shui Wai will be permanently encroached (Figure 13.2). This fishpond would be liable to permanent direct impacts from the project. Within the site of the alignment, fish culture will not be possible during the construction or operational phases. This will constitute a permanent loss of fishponds. The total area of the affected ponds would be about 0.05 ha. This figure constitutes a permanent loss of less than 0.005 % of the 1060 ha of fishponds in Hong Kong (AFCD 2001) [29].

 

This fishpond, though classified as active due to the presence of aerator and the conditions of the pond bunds, was isolated from other active fishponds in the area. Given the small percentage of loss and its isolated location, the impact on inland fishpond culture in Hong Kong from the loss of this part of one fishpond due to the proposed project is ranked as minimal.

 

None of the other alignments or pumping stations would cause any permanent direct impacts to fishponds.

 

An area of 0.20 ha distributed in three fishponds (mainly underneath pond bunds) at Shan Pui will be temporarily occupied as works areas (Figure 13.2). This area, however, will be reinstated after the construction, and only consistute a temporary direct impact.

 

16.4.1   Tin Shui Wai and San Wai Areas (Alternative 2A-1T)

This element includes a sewer alignment starting from Ha Tsuen, passing through Tin Shui Wai and ending at Yuen Long STW. 

 

Direct impacts arised from this element include a permanent loss of 0.05ha active fishpond area and a temporary loss of 0.20 ha active fishpond area.

 

The only permanent direct impact predicted to occur to aquaculture fisheries is the permanent direct loss of part of an active fishpond as a result of the construction of the sewerage alignment Alternative 2A-1T.  It is calculated that approximately less than 0.05 ha of the fishpond will overlap with the alignment and thus will be lost through construction.  Based on the size of this loss, this loss of fishpond is ranked as minimal deemed acceptable.

 

The majority of the proposed sewerage alignment will be constructed along the roads and main drainage channels that are urbanised and disturbed. Three active fishponds within WCA in Shan Pui, however, are adjacent to the section of sewer alignment running along the Yuen Long STW western boundary. Due to the need of work areas during the construction of the sewer, a total of 0.20 ha fishpond areas (mainly underneath pond bunds), distributed along the three fishpond’s edges which are in contact with the sewer alignment, will be occupied during the constuction phase. These fishpond areas will be reinstated after the construction works are finished. Based on the size of this loss and its limited duration of loss, this impact on fishpond is ranked as minor.

 

One abandoned fishpond in Shan Pui is close to the further westward section of the alignment. The sewer alignment is also near one active fishpond and one abandoned fishpond in San Wai. Though the sewers are proposed to be buried underneath footpaths and roads and the ground surface will be reinstated afterwards, site runoff from the works areas might affect the fishponds and consistute indirect impacts. Given the nature of the impacts and the small number of fishponds potentially affected, the impact is ranked as minor.

 

No direct or indirect impact on fishponds would be expected from construction of the pumping station.

 

16.4.2   Ngau Tam Mei and San Tin Areas (2A-2T and 2B-1T)

This element includes a sewer alignment which starts at Siu Hum Tsuen, runs southwest along Castle Peak Road till Ngau Tam Mei, switches to the embankment of the newly constructed 100CD drainage channel, and ends at 60CD drainage channel.

 

No fishponds would be directly affected by the alignment. The majority of the proposed sewerage alignment will be constructed along the roads and main drainage channels that are urbanised and disturbed. For the majority of the sewer alignment, there is also no fishpond near or close to the alignment, except the section of alignment close to the sewage treatment works in Ngau Tam Mei in where the alignment is adjacent to six active fishponds. Near Mai Po Lo Wai, the alignment is close to another active fishpond. Two abandoned fishponds in San Wai also near a section of alignment.

 

The sewers are proposed to be buried underneath footpaths and roads and the ground surface will be reinstated afterwards. Site runoff from the works areas might affect the fishponds. Given the nature of the impacts and the small number of fishponds potentially affected, the impact is ranked as minor.  

 

16.4.3   Lau Fau Shan and Mong Tseng Areas (2A-3T)

This element includes a sewer alignment starting from Lau Fau Shan, and another one starting at Mong Tseng. These two sections join at Sha Kong Wai Tsai, cross the Tin Shui Wai Western Drainage Channel, and join the sewer of 2A-1T. 

 

There is a small area of sea and coastline within the assessment area, located at the northwest end of this part of the assessment area. This marine area, however, is away from the alignment and would not be subject to any direct or indirect impact from the project.  

 

The majority of the proposed sewerage alignment will be constructed along the roads and embankment of main drainage channels that are urbanised and disturbed.  No fishponds would be directly affected by the alignment. For the majority of the sewer alignment, there is also no fishponds near or close to the alignment, except the section at Mong Tseng where the alignment will follow an existing road which is adjacent to one active and two abandoned fishponds.

 

The sewers are proposed to be buried underneath footpaths and roads and the ground surface will be reinstated afterwards. Site runoff from the works areas might affect the fishponds. Given the nature of the impacts and the small number of fishponds potentially affected, the impact is ranked as minor.  

 

16.4.4   Shap Pat Heung Area (2B-2T)

As described above, presently there are only 0.75 ha of active fishponds within this part of the assessment area. Moreover, all active fishponds are located close to the southern assessment area boundary and far away from the locations of all proposed works. No land resumption process would be needed for the fishponds within this part of the assessment area. No direct or indirect impacts on fishponds or their operations would be expected from the project.

 

16.5      Impact Avoidance and Mitigation Measures for Construction Phase

In accordance with the guidelines in the EIAO-TM on fisheries impact assessment the approaches to mitigating impacts to fisheries, in order of priority, are avoidance, minimising, and compensation.

 

Only 0.05 ha of fish pond will be permanently lost for the entire project, and 0.20 ha of fish pond areas will be temporarily occupied during construction.  As the proposed construction of the sewerage system and pumping stations are not predicted to have a significant or unacceptable impact on aquaculture fisheries resources and operations in the assessment area, no fisheries-specific mitigation measures are required.

·      

16.5.1   Tin Shui Wai and San Wai Areas (Alternative 2A-1T)

Permanent direct impacts of this project to fish culture in fishponds in San Wai would be minor. No mitigation would be required.

 

Standard site practice should be enforced to minimise the site runoff disturbance to the surroundings. Sedimentation during construction should be prevented by erection of sediment barriers and operation of siltation traps in works sites close to fishponds which could potentially be affected.  Temporary work sites/disturbed areas immediately should be reinstated after completion of the construction works. The work site boundaries should be checked regularly to ensure that they are not exceeded and that no damage occurs to surrounding areas.

 

16.5.2   Ngau Tam Mei and San Tin Areas (2A-2T and 2B-1T)

Standard site practice should be enforced to minimise the site runoff disturbance to the surroundings. Sedimentation during construction should be prevented by erection of sediment barriers and operation of siltation traps in works sites close to fishponds which could potentially be affected.  Temporary work sites/disturbed areas immediately should be reinstated after completion of the construction works. The work site boundaries should be checked regularly to ensure that they are not exceeded and that no damage occurs to surrounding areas.

 

16.5.3   Lau Fau Shan and Mong Tseng Areas (2A-3T)

Standard site practice should be enforced to minimise the site runoff disturbance to the surroundings. Sedimentation during construction should be prevented by erection of sediment barriers and operation of siltation traps in works sites close to fishponds which could potentially be affected.  Temporary work sites/disturbed areas immediately should be reinstated after completion of the construction works. The work site boundaries should be checked regularly to ensure that they are not exceeded and that no damage occurs to surrounding areas.

 

No adverse temporary or permanent impacts of the proposed project to the existing capture fisheries and mariculture near Lau Fau Shan are expected. No impact mitigation would be required.

 

16.5.4   Shap Pat Heung Area (2B-2T)

No mitigation measure is required as no direct or indirect impacts are anticipated.

 

16.6      Impact Identification and Evaluation for Operational Phase

No operational phase impacts are expected to aquaculture fisheries resources and operations as a result of the operation of the sewerage system and pumping stations.

 

16.7      Impact Avoidance and Mitigation Measures for Operational Phase

No mitigation measure is required as no operational phase Impacts are expected.

 

From the information presented above, no adverse fisheries impact associated with the proposed project is expected. An evaluation of the impact in accordance with the EIAO-TM Annex 9 is presented in Table 16.2.

 

Table 16.2:  Evaluation of fisheries impacts in accordance with EIAO-TM Annex 9

Impacts

Criteria

Nature of impact

 

Size of affected area

 

Loss of fisheries resources/ production

Destruction and disturbance of nursery and spawning grounds

Impact on fishing activity

 

Impact on aquaculture activity

 

Tin Shui Wai and San Wai Areas (Alternative 2A-1T)

Construction phase

Land work area

Permanent loss of part of a fishpond due to conscturction of sewers

0.05 ha of active fishpond to be resumed

About 0.05 ha fishpond area will be lost.

No impact on nursery and spawning grounds would be caused.

NA

0.05 ha of fishpond in San Wai would be affected by the project.

Land work area

Temporary loss of 0.20 ha of fishpond area due to the need of works areas

0.20 ha of active fishpond to be temporary occupied

About 0.20 ha fishpond area will be temporary lost.

No impact on nursery and spawning grounds would be caused.

NA

0.20 ha of fishpond areas in Shan Pui would be temporarily affected by the project.

Land work area

Site runoff

5 active fishponds and 2 abandoned fishponds are potentially subject to site runoff

NA

No impact on nursery and spawning grounds would be caused.

NA

Water quality inside fishponds might be affected

Operational phase

Sewage

Alignment

Permanent occupation of fishponds.

0.05 ha of active fishpond

About 0.05 ha fishpond area will be lost.

No impact on nursery and spawning grounds would be caused.

NA

Permanent loss of 0.05 ha of fishpond in San Wai

Ngau Tam Mei and San Tin Areas (2A-2T and 2B-1T)

Construction phase

Land work area

Site runoff

7 active fishponds and 2 abandoned fishponds are potentially subject to site runoff

NA

No impact on nursery and spawning grounds would be caused.

NA

Water quality inside fishponds might be affected

Operational phase

No impact

NA

NA

NA

NA

NA

NA

Lau Fau Shan and Mong Tsang Areas (2A-3T)

Construction phase

Land work area

Site runoff

1 active fishponds and 2 abandoned fishponds are potentially subject to site runoff

NA

No impact on nursery and spawning grounds would be caused.

NA

Water quality inside fishponds might be affected

Operational phase

No impact

NA

NA

NA

NA

NA

NA

Shap Pat Heung Area (2B-2T)

Construction phase

No impact

NA

NA

NA

NA

NA

NA

Operational phase

No impact

NA

NA

NA

NA

NA

NA

 

Although there are a number of concurrent projects that are currently implemented or planned, each project will provide its own mitigation measures. Cumulative impacts predicted to arise from the proposed project in conjunction with concurrent projects are not expected to result in greater adverse impacts to fisheries sensitive receivers than would impacts arising from the concurrent projects independently.

 

There are no residual impacts expected to occur to aquaculture fisheries as a result of the construction and operation of the proposed sewerage system and pumping stations.

 

As direct impacts to fishponds are predicted to be minimal while the indirect impacts during construction phase to be minor, the development of a monitoring and audit programme to assess the effects of the proposed project on fisheries is not considered necessary. Monitoring and audit activities designed to detect and mitigate any unacceptable impacts to water quality will also serve to protect against temporary unacceptable impacts to fisheries resources.

 

Deep Bay is facing long-term pollution problems which threaten the sensitive ecosystem in Deep Bay. HKSAR Government is planning to substantially reduce pollution loadings in Deep Bay. Under the Yuen Long/Kam Tin Sewerage Master Plan, sewage networks will be provided to unsewered villages and new developments, and sewage effluents from Yuen Long and Kam Tin will be transported out of Deep Bay to the better flushed water in Urmston Road for disposal (EPD 2001). The proposed project is an important component of the Plan.

 

Though Grade A active fishponds were identified within the assessment area with the majority concentrated to the Shan Pui, Nam Sang Wai, Tai Sang Wai and San Tin, the majority of assessment area appears to be degraded through urbanisation and development. None of the sewer alignment or the pumping station locations would constitute permanent direct impacts to any Grade A active fishponds. Only a fraction (0.05 ha) of a Grade C fishpond in San Wai would be subject to direct loss. Potential impacts to fisheries resources and operations may arise from permanent loss of fishponds. Due to the small percentage compared to the overall resources in Hong Kong, permanent losses of fisheries resources due to the project are predicted to cause minimal impacts to HKSAR fisheries. The impact is minimal and acceptable.

 

A total area of 0.20 ha will be temporarily occupied at three Grade A fishponds at Shan Pui during the construction phase. These fishponds will be reinstated after the construction works and thus the impact is minor and acceptable.

 

Based on the above impact assessment, no unacceptable impacts to aquaculture fisheries resources and operations are expected to occur as a result of the construction and operation of the proposed sewerage system and pumping stations.

 

 

 

 


17.0      Environmental Monitoring and Audit (EM&A)

An EM&A programme during the construction and operational phases will be prepared in accordance with the findings of EIA report, Study brief, “Environmental Monitoring and Audit - Guidelines for Development Projects in Hong Kong and Annex 21 of the TM-EIAO” to ensure that the predicted impacts are within the relevant standards. Contingency plans will also be incorporated into the EM&A manual in case that Action or Limit Levels are exceeded. In addition, the implementation schedule (Appendix 17.1) will clearly identify the actions and responsibility of different parties in the design, construction and operational stages. The implementation schedules will form the basis of the Environmental Permit conditions and contractual requirements to be formulated at the detailed design stage.

 

17.1      Air Quality Impact

17.1.1   Construction Phase (Air Quality)

Dust suppresion requirements given in the Air Pollution Control (Construction Dust) Regulation have been proposed.  In order to ensure the impact is minimal, EM&A requirements have been proposed.  Monitoring locations are presented in Table 17.1 and the EM&A details are described separately in the Environmental Monitoring and Audit (EM&A) Manual.

Table 17.1:  Representative air quality monitoring locations

Package

AML ID

EIA ASR Ref

Description

Land Uses

Approx. Distance to Sewer/Pumping Station (m)

Tin Shui Wai Area (2A-1T)

AM1

AT11

Tin Wah Estate, Wah Long House

R

26

AM2

AT21

Jade Court, Block A

R

15

AM3

AT15

Maywood Court, Block 8

R

32

AM4

AT29

Dunwell Group

C

53

Lau Fau Shan Area (Alternative 2A-3T)

AM5

AL01

Deep Bay Road, workshop

C

17

AM6

AL07

San Hing Tseun, No.37

R

16

AM7

AL13

Tin Ying Road, Interin Housing, Block 2

R

128

AM8

AL24

Mong Tseng Tseun, No.1

R

18

Ngau Tam Mei and San Tin Areas (2A-2T and 2B-1T)

AM9

AN02

Kam Pok Road, Man Yuen Chuen No.19

R

12

AM10

AN10

Castle Peak Raod Tam Mei, village house

R

32

AM11

AN15

Ngau Tam Mei, village house

R

25

AM12

AN23

Castle Peak Road Mai Po, No.55, Koon Ying School

G/IC

18

AM13

AN29

Castle Peak Road San Tin No.128/ Future School

G/IC

36

 

AM14

AN40

Fan Tin Tseun, Lun Fung Ming Ancestral Hall

G/IC

11

 

AM15

AN46

Ka Lung Road, village house

R

10

 

AM16

AN51

Ka Lung Road, No.54, San Tin Barrack

G/IC

16

Shap Pat Heung Area (2B-2T)

AM17

AS04

Sha Ha Tseun, No.548

R

26

AM18

AS17

Muk Kiu Tau Tseun, No.1

R

18

AM19

AS23

Pak Sha Tseun, No.62

R

32

AM20

AS25

Wong Nai Tun Tseun, No.47C

R

16

AM21

AS36

Shun Ching San Tseun, No.211

R

12

 

AM22

AS40

Shui Tsiu San Tseun, No.181

R

19

 

AM23

AS52

Shung Ching San Tseun

R

20

 

AM24

AS64

Tai Kei Leng, No.702

R

13

 

AM25

AS70

Tong Tau Po Tseun, No.1

R

24

 

17.1.2   Operational Phase (Air Quality)

With the provision of adequate mitigation measures, there is no EM&A requirement during the operational phase.

 

17.2      Noise Impact

17.2.1   Construction Phase (Noise)

A construction noise assessment has been undertaken with the consideration of cumulative impacts arising from other projects proposed in the vicinity of the study area. Unmitigated construction noise would cause exceedance of the daytime construction noise criteria. Mitigation measures such as adopting quiet plant, limiting the use of PME, using of temporary barriers along site boundary, and employing temporary and movable barrier close to construction plants for sewage pumping station construction have been recommended. However, residual impact at some NSRs are predicted.

The recommended monitoring locations are presented in Table 17.2 and requirement are detailed in the Environmental Monitoring and Audit (EM&A) Manual. The effectiveness of on-site control measures could also be evaluated through the monitoring. All the recommended mitigation measures should be incorporated into the EM&A programme for implementation during the construction phase.

Table 17.2:  Representative noise monitoring locations

Package

NML ID

EIA NSR Ref

Represent No of Dwelling in the area

Remark/Description

Tin Shui Wai Area (2A-1T)

NM1

NT08

9

-

NM2

NT09

-

school

NM3

NT15

256

-

NM4

NT21

3

-

Lau Fau Shan Area (Alternative 2A-3T)

NM5

NL03

-

-

NM6

NL08

15

-

NM7

NL13

3

-

NM8

NL22

6

-

Ngau Tam Mei and San Tin Areas (2A-2T and 2B-1T)

NM9

NN02

42

-

NM10

NN09

21

-

NM11

NN14

3

-

NM12

NN23

87

-

NM13

NN27

12

-

 

NM14

NN29

3

-

 

NM15

NN30

-

-

 

NM16

NN35

 

-

 

NM17

NN40

12

-

 

NM18

NN46

6

-

 

NM19

NN51

9

-

Shap Pat Heung Area (2B-2T)

NM20

NS01

3

-

NM21

NS11

3

-

NM22

NS17

3

-

NM23

NS21

3

-

NM24

NS26

12

-

NM25

NS31

6

-

 

NM26

NS35

6

-

 

NM27

NS40

15

-

 

NM28

NS46

15

-

 

NM29

NS51

9

-

 

NM30

NS52

12

-

 

NM31

NS54

3

-

 

NM32

NS60

3

-

 

NM33

NS64

12

-

 

NM34

NS72

21

-

 

NM35

NS37b

12

-

 

NM36

NS42a

9

-

 

NM37

NS70a

3

-

 

NM38

NS49b

-

School

 

17.2.2   Operational Phase (Noise)

In order to ensure that compliance with the noise limits specified in the report are achieved, noise commissioning at the site boundary and louvres at all the proposed sewage pumping stations shall be conducted as a requirement for Practical Completion.  The measurement data during commissioning should be submitted to the Environmental Team (ET) Leader for checking against the noise design criteria.

 

17.3      Water Quality Assessment

With implementation of the recommended mitigation measures, the potential water quality impact will be minimal.  No EM&A requirement will therefore be required during construction and operational phases.

 

17.4      Waste Management

The Contractor shall prepare a Waste Management Plan and execute the requirements according to the EM&A manual.  A trip-ticket system should be established in accordance with the Works Bureau Technical Circular No. 5/99 to monitor the disposal of public fill and solid wastes at public filling facilities and landfills, and to control fly-tipping.  During site inspections and submission review, the ET Leader shall pay special attention to the issues relating to waste management, and check whether the Contractor has followed the relevant contractural clauses and satisfied the procedures as stipulated under the legislation of Hong Kong.

 

17.5      Land Contamination Implications

With implementation of the recommended mitigation measures, health and safety precaustionary measures and confirmatory test, the potential impact will be minimal.  No special EM&A requirement will be required during construction and operational phases.

 

17.6      Ecological Assessment

The implementation of standard site practice stated in Section 13.6 of the EIA, such as use of quiet machinery and prevention of site runoff, shall also be checked as part of the environmental monitoring and audit procedures during the construction period. 

 

The following recommendations are also made for the Works Package (Figure 13.5).

 

17.6.1   Designated Elements

·     Restriction of construction period to April through October for elements within WCA, i.e. AP1and 430m of AS1, to minimise disturbance to wintering birds;

·     Reinstatement of temporary works area to its original conditions, in particular, for the three fish ponds along AS1. Appropriate construction method will be adopted to ensure that no dewatering of nearby fishpond is required. Such construction method shall be agreed by DSD before commencement of works.

·     Provision of a detailed replanting plan during the detailed design stage for the 0.35ha of replanting area at San Pui Ponds to compensate for the loss of 0.23ha of 60CD mitigation planting area to YLEPS (See Section 13.6.1 for details). 

 

The above conditions shall be complied as part of the construction contract.

 

17.6.2   Non Designated Elements

·     Restriction of construction period to April through October for elements within WCA, i.e., section of S1 to minimise disturbance to wintering birds;

·     Restriction of construction period to September through March for sewer alignment sections S4/S5 within 100m from Mai Po Village and Mai Po Loong Egretries to minimise disturbance to the egretries during the breeding season;

·     Reinstatement of temporary works area to its original conditions, in particular, for mixed woodland habitats along AS3.  The contractor shall refer to the results of vegetation surveys conducted at the mixed woodland habitat by DSD during the detailed design phase for reinstatement.

 

The above conditions shall be complied as part of the construction contract.

 

No other ecology-specific measures are considered necessary.

 

 

17.7      Landscape and Visual Impacts

With implementation of the recommended mitigation measures, the potential impact will be minimal.  No EM&A requirement will be required during construction and operational phases.

 

17.8      Cultural Heritage Assessment

17.8.1   Archaeology

The assessment has concluded that the construction of the proposed works may adversely impact on areas of archaeological potential in areas not available at the field evaluation stage. :

The mitigation recommendation is the following:

1.       Pre-testing is required at the following locations:

§     Mong Tseng Tsuen PS (non-designated element).  The pre-testing should comprise of the hand excavation of a minimum of one test pit measuring no less than 2 by 2 meters; and

§     Sewer alignment north of Tung Tau Tsuen (non-designated element).  The pre-testing should comprise of a field investigation with a minimum of 20 auger hole tests and hand excavation of two test pits measuring no less than 2 by 2 meters.

Pre-testing should be undertaken prior to construction, but after land resumption at Mong Tseng and north of Tung Tau Tsuen and surface removal of concrete and asphalt at north of Tung Tau Tsuen.

2.       Archaeological monitoring is recommended at the sewer alignment around the historical village of Tai Tseng Ng Uk Tsuen, Tai Tseng Wai and Shing Uk Tsuen (non-designated element) (see Figure 15.48).  The archaeological evaluation and archaeological monitoring should be conducted by a qualified archaeologist, who should be licensed by the Antiquities Authority before the evaluation or archaeological monitoring takes place. This licensing procedure is a statutory requirement stated in Sections 12 and 13 in the Antiquities and Monuments Ordinance (Cap. 53). The contractor should inform AMO the time schedule of the archaeological evaluation or archaeological monitoring and notify AMO two weeks prior to the commencement of the evaluation or archaeological monitoring so as to allow AMO to arrange the on-site monitoring.  The licensed archaeologist, when conducting the archaeological monitoring during construction phase, should adopt a minimum 5% sampling strategy.

 

Finally, if the conforming scheme 2A-IT of the Yuen Long sewage treatment works effluent pipeline is preferred, an archaeological impact assessment will have to be conducted prior to construction.

 

17.8.2   Built Heritage

Construction Phase

 

The following resources will require mitigation during the construction phase:

 

i) Lau Fau Shan to Mong Tseng

 

Lau Fau Shan Road

 

Modern shrine AAHB-21: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works area by metal barriers.

 

ii) San Tin to Ngau Tam Mei

 

Fan Tin Tsuen

 

Man Lun Fung Ancestral Hall AAHB-405: As the works are in close proximity to the southwestern wall of the ancestral hall, which is a Declared Monument, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended. The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures

 

Shrine AAHB-419: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Ming Yuen Tong AAHB-433: As the works are in close proximity to the southeastern wall of the ancestral hall, which is a Grade II building, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended. The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

Shun Yue Tong (Grade II) and San Yeh Man Tong (Grade I) AAHB-486 and 487: As the works are in close proximity to the southeastern walls of both of the ancestral halls, the contractor must carry out a condition survey of both of the buildings. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended.  The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

Castle Peak Road (San Tin to Mai Po)

 

Temple and shrine AAHB 227: The temple, although renovated contains historical architectural elements and is located directly on the edge of the works area. Hence, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended. The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures. The shrine is located at a sufficient distance as to not require any protective measures during the construction phase. Access to the temple and shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Modern Village Gates AAHB-231 and 240: The base of the gates should be provided with a protective covering in the form of heavy duty plastic sheeting, supported by scaffolding where necessary.

 

Castle Peak Road (Yau Mei Tsuen)

 

Shrine AAHB-242: The shrine is located at a sufficient distance as to not require any protective measures during the construction phase. Access from Castle Peak Road should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

iii) Shap Pat Heung

 

Kung Um Road

 

Shrine AAHB-262: The shrine should be provided with a minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Tai Tong Road

 

Modern Village Gates AAHB-129, 131,153,162, 164 and 211: The base of the gates should be provided with a protective covering in the form of heavy duty plastic sheeting, supported by scaffolding where necessary.

 

Shrine AAHB-207: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Tai Shu Ha Road East

 

Shrine AAHB-224: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Temple AAHB-226: The entrance to the temple is located directly from Tai Shu Ha Road, access from the road should be maintained throughout the construction phase.

 

(iv) Yuen Long Effluent Pipeline

 

Shrine AAHB-357: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Operational phase

 

·     The following resources will require mitigation measures for the operational phase:

·     Mong Teng Tsuen (village structures, AAHB-29 to 53)

·     Fan Tin Tsuen (Ming Yuen Tong AAHB-433 and Man Lun Fung AAHB-405)

·     Tai Shu Ha Road East, Nga Yiu Tau  (Tin Hau Temple AAHB-226)

 

The mitigation will consist of landscaping of the area around the pumping station should include planting of foliage complimentary to the existing environmental setting, in order to screen the proposed pumping station and minimise visual impacts. The colour treatment of the proposed pumping station should minimise visual impact.

 

Buddhist Blessing Stones

There will be no impacts to Buddhist blessing stones during either the construction or operational phases, therefore no mitigation measures will be necessary.

 

Graves

There will be no impacts to any of the surveyed graves in the study area or to those located within the Cassino camp during either the construction or operational phases, therefore no mitigation measures will be necessary.

 

Cultural and Historical Landscape Features

No cultural or historical landscape features will be impacted by the project during either the construction or operational phase; therefore, no mitigation measures will be required.

 

 

17.9      Fisheries Assessment

With implementation of the site practices to control site runoff during construction, the minor indirect impact would be acceptable.  No EM&A requirement will be required during construction and operational phases.

 


18.0      Summary of Environmental Outcomes

18.1      Air Quality Impact

Similar to the previous EIA report (Designated Project) on CE31/99 “Yuen Long and Kam Tin Sewerage and Sewage Disposal Stage 1”, the sewer and rising mains will be constructed in 50m segments. With such small scale of construction works, the potential dust impact would be limited and short term in nature.  Regarding the sewage pumping stations, most part of the structures will be constructed underground while the pumping station building will be about 1-storey above ground level.  Scaffolding with effective dust screens, sheeting or netting and automatic water spraying equipment shall be erected around the perimeter of the building during construction.  With the implementation of proper contractual clauses and Best Site Practice controlled within the APC (Construction Dust) Regulation, adverse dust impact is not anticipated.  An effective EM&A system is proposed to ensure the dust impact during construction phase is controlled within the legislative criteria.

 

During the operational phase, major air quality impact would be related to the potential odour emissions from Sewage Pumping Stations. An odour removal filter with the following H2S removal efficiency has been recommended in the EIA report:

·     of not less than 99.5% for AP1 SPS of 2A-1T.

·     of not less than 99.5% for P1 to P5 SPS of 2A-2T and 2B-1T.

·     of not less than 95% for all SPS at 2A-3T (A1 to A2); and

·     of not less than 95% for all SPS at 2B-2T (B1 to B7).

 

Owing to the large setback distance of more than 400m and conveying of treated sewer at YLEPS, it is confirmed that YLEPS is not a potential odour source.

 

The entire SPS; especially wet wells and screening collection areas should be enclosed in a building structure (Similar to that shown in Figure 14.62 of the EIA report) and the discharge point of the odour removal system should be directed away from the adjacent sensitive uses, and the discharge height should not be less than those assumed in Table 7.4. With the implementation of the recommended odour control measures, the computer dispersion modelling results showed that the odour levels at the air sensitive receivers around the SPS would be well below the EPD odour criterion.

 

18.2      Noise Impact

The construction noise impact of the project is due to the construction of the sewerage and the pumping station. There will also be cumulative construction noise impact due to the concurrent construction activities in the vicinity of the project site.

 

The distance of the most identified existing and future noise sensitive receiver are located very close to the work fronts. With the use of quieter plant, temporary noise barrier / enclosure, reschedules the construction program and regrouping the construction activities, residual construction noise impacts are still predicted at some noise sensitive receivers. However, the adverse residual impact will be temporary and will last for few days in daytime only. It is considered as acceptable.

 

During the operational phase, with the use of silencer, enclosure and acoustic louvre in the pumping station, adverse residual impact is not anticipated.

 

18.3      Water Quality Impact

Potential impacts during the construction phase will be arisen from pollutants in surface run-off, which may enter surface water or the stormwater drain directly before discharging into Deep Bay. Mitigation measures recommended in ProPECC PN 1/94 Construction Site Drainage will be implemented. There will also be cumulative construction water quality impact due to the concurrent construction activities in the vicinity of the project site. Given that the mitigation measures in their corresponding EIA studies (if designated projects) or ProPECC PN 1/94 are proper installed, cumulative impact is also not anticipated.

 

The normal operation of the Yuen Long / Kam Tin Sewerage and Sewage Disposal Stage 2 works will result in improvement of water quality in both the inland and marine waters in the NWWCZ and Deep Bay WCZ after the treatment of the San Wai Sewage Treatment Plant. Therefore no other mitigation measures will be required. During the operational phase, potential water quality impact will be arisen from emergency discharge from pumping station and operation of the rising mains. Mitigation measures are proposed as follows:

 

Emergency Operation of Pumping Stations

·     The discharge point of the overflow bypass should be below the low water mark (i.e. location of minimum water level in stream in dry season);

·     The discharge point of the overflow bypass should be away from sensitive receivers such as fish ponds, water gathering grounds, country parks, nature reserves, sites of special scientific interest, marine parks/marine reserves, streams with water for human consumption, etc.;

·     A contingency plan for emergency discharge shall be developed;

·     The overflow bypass should be operated only in an emergency, such as prolonged power failure.  Overflow mechanism must not occur to facilitate routine maintenance on a regular basis;

·     If the pumping station is unmanned, a telemetry system should be provided to the nearest manned station/plant so that swift actions could be taken in the case of malfunction of the unmanned facilities;

·     Hand-cleaned screens should be provided at the overflow bypass to prevent the discharge of floating solids into receiving water bodies.  The clear spacing of the bar screen should normally be about 25mm;

·     Standby pump should be provided to facilitate maintenance and repairing of equipment; and

·     Dual (back-up) power supply should be provided.  Dual power supply could be in the format of ring main, or an automatic-operated emergency generator with sufficient capacity to cope with the demand loading of the essential plant equipment.

 

Emergency Operation of Rising Main

·     Twin rising mains are provided for backup and repairing purpose

·     Should the twin rising mains be failure, tankers will be used to store the emergency discharge and transport to the YLSTW or SWSTW for disposal.

 

With the implementation of the above mitigation measures, water quality impact during the operational phase is not anticipated.

 

18.4      Waste Management Implications

The following quantities of waste are expected to arise during the construction of the proposed gravity sewer and pumping station: public fill of 111,460m3(46,168m3 from 3 work items of Designated Elements and 65,292m3 from 38 work items of Non-designated Elements under 4 packages); and chemical waste (less than hundred liters per month); and general refuse.

 

Good waste management practices have been recommended to ensure that adverse environmental impacts from the handling and disposal of construction and operational wastes are prevented or minimized.  A separate C&DMMP will be prepared by the DSD project office for departmental vetting before upgrading of this project to Category “A” in Public Works Programme. An overall Waste Management Plan (WMP) should incorporate DEP’s comments and be approved by DEP. Since the project site is located closed to the WBA or WCA, it is important to put control clauses in the contract to disposal waste away from the ecological sensitive areas.  The WMP should also include the following:

·     The type of C&D generated;

·     The amount for each type of C&D material;

·     The location of waste sorting; and

·     The location of disposal.

 

No unacceptable environmental impacts will result from the construction and operation of the proposed sewerage and Pumping Stations.

 

18.5      Land Contamination Impact

The preliminary investigation identified the land uses adjacent to the proposed alignment of the sewers/raising mains with the minimal potential to give rise to land contamination, as defined in the EPD’s guidance documents. As the various premises in question are all fairly small in size, the proposed sewers/raising mains alignment and the location of pumping stations do not lie within the potential contaminated premises, and the land contamination potential is judged to be localised, the overall contamination concerns to the Project site area are considered to be very low.

 

Although the risk of land contamination of the Project site area is very low, it is still recommended to conduct the “Confirmatory Soil Test” during the excavation to further safeguard the construction workers.  Since great portion of the alignments are located underneath major roads, road closure for confirmatory testing is not feasibility.  Therefore, it is suggested that the testing should be conducted during detailed design stage or the commencement of work when site access is still feasible.

 

18.6      Ecological Impact

Most of the study area, particularly the area to be directly affected by the proposed Project is highly urbanised and degraded by existing and on-going development.  Habitats found within the study area include plantation, mixed woodland, grassland/shrubland, cultivated land/orchard, fishpond, stream/channel, mangrove, and disturbed/urbanized/wasteland areas.  Two species of plants and 4 species/groups of birds of conservation interest were recorded. 

 

The designated elements would cause a permanent loss of 0. 39 ha of urbanized/disturbed/wasteland and 0.23ha of plantation for construction of pumping stations, and a temporary loss of 0.24 ha of urbanized/disturbed/wasteland and 0.20 ha of fishponds for construction of sewers.  There will be no-net-loss in wetland area at the WCA and CA.  After implementation of mitigation measures, there is no adverse impact.

 

The non-designated element would cause a permanent loss of 0.95 ha of urbanized/disturbed/wasteland, 0.05 ha of fishponds and 0.12 ha of cultivated land and a temporary loss of 25.49 ha of urbanized/disturbed/wasteland, 0.46 ha of mixed woodland, 0. 28 ha of shrubland/grassland, 0.02 ha of plantation and 0.14 ha of cultivated land.  The overall ecological impacts are ranked as minor.  Standard site practice and recommendations to each works package are made and no residual impacts are anticipated.

 

A detailed tree survey should be performed during the detailed design phase (with the ultimate alignment) by the DSD at the mixed woodland (Item AS3) in order to provide information for site reinstatement by the contractor.

 

It is recommended that the construction period of items within WCA (Package 2A-1T alternative), i.e. the pumping station AP1 and 430m of AS1 be restricted to April through October to avoid the potential disturbance to wintering waterbirds.  In order to reduce the impact on the nearby fishpond within WCA, laying of sewer will be conducted in 20m segment.  The construction works will also be scheduled during non rainy days. Appropriate construction method will be adopted to ensure that no dewatering of nearby fishpond is required. Such construction method shall be agreed by DSD before commencement of works.

 

Replanting area would also be provided to compensate for the loss of 60CD mitigation planting area on a like-to-like basis by using the native species recorded in the existing 60CD planting (Table 13.28). A potential replanting area is located at Shan Pui Ponds.  These abandoned ponds are within WCA and are government ponds. These ponds form an island between 60CD and are accessible by boat.  The grassy area highlighted in Figure 13.5 is above high tide zone and will not be subject to tidal action.  About 0.35 ha will be planted, which can compensate for the loss from YLEPS at a 1.5:1 ratio to off-set the time loss and to reduce of risk of poor survival.  Saplings of native tree species recorded in 60CD plantation including Sapium sebiferum, Hibiscus tiliaceus and Celtis tetrandra subsp. sinensis and others including Macaranga tanarius and Melia azedarach will be used in the replanting area. Maintenance schedule should be specified in the landscape contract and should include irrigation and weeding on a bimonthly basis for the first year of establishment to enhance survival.  Tree seedlings dead within the first year should be replaced by the landscape contractors.  Upon completion of the landscape contract the plantation should be handed over to AFCD.  A detailed replanting plan should be included during the detailed design stage.

 

It is also recommended that the construction period of items within WCA (Package 2A-2T and 2B-1T), i.e. 560m of S1 along 100CD, be restricted to April through October to avoid the potential disturbance to wintering waterbirds.  Due to the potential noise disturbance from construction works, the construction period of the alignment sections within 100m from Mai Po Village and Mai Po Loong egretries shall be restricted to September through March to avoid breeding season as possible to reduce disturbance to breeding birds.

Work sites/disturbed areas shall be reinstated immediately after completion of the construction works, in particular, through on-site tree/shrub planting along the woodland section at Tin Shui Wai, and 3 fishponds within WCA.

 

On top of the EIAO application, a rezoning request to change the landuse for some pumping stations are required by DSD during detailed design stage.  Supporting ecological impact assessment is required to justify the case. Without the approval from the Town Planning Board, land right for construction will not be given.

 

18.7      Landscape and Visual Impact

Construction Phase mitigation measures shall include the following mitigation measures (note: In all cases, the proposed mitigation measures for designated and non-designated elements will be the same):

·     Regular checks should be carried out to ensure that the work site boundaries are not transgressed, hoardings are properly maintained and that no damage is being caused to the surrounding areas.

·     Topsoil (uncontaminated), where identified, should be stripped and stored for re-use in the reinstatement of topography and soft landscape, where practical.

·     The potential for soil erosion should be reduced by minimising the extent of vegetation disturbance on site and by providing a protective cover (e.g. plastic sheeting or a grass cover established by hydroseeding) over newly exposed soil.

·     Waste disposal and cleansing of equipment should be strictly controlled on site to prevent ground contamination.

·     All existing trees shall be carefully protected during construction.  Detailed Tree Protection Specification shall be provided in the Contract Specification.  Under this Specification, the Contractor shall be required to submit, for approval, a detailed working methodology for the protection of trees prior to undertaking any works adjacent to all retailed trees.

·     Trench excavation for pipe laying to be located a minimum of 2 m from the nearest part of roadside tree trunks.

·     Reinstatement of turf grass cover disturbed during excavation for installation of pipeline under the waterway.

·     Reduce construction time to a minimum.

·     Transplantation of affected trees to holding nursery with the view to relocation within the immediate vicinity towards the completion of construction works.

·     Ensure requirements for stockpiles are reduced wherever possible and that stockpiles do not transgress works site boundaries.

·     Ensure vegetation removal at any site of trench works, directional drilling or construction of pumping station does not include unnecessary trimming or disruption of tree roots and branches of adjacent vegetation.

 

Operational Phase measures shall include the following mitigation measures (note: In all cases, the proposed mitigation measures for designated and non-designated elements will be the same):

·     Tree planting to compensate for any affected trees.

·     Turfing/grassing of the roof of the YLEPS (Figure 14.66).

·     Pumping Stations located so as to avoid sensitive landscape features as far as practicable.

·     Pumping stations should be designed so as to complement the surrounding rural environment.  In particular, a clay brick tile should be used as a building finish to reduce visual impact of the structures.  This treatment is shown in Figures 14.62 to 14.65 inclusively.

·     Soft landscape works around the pumping stations will include multi-layered trees and shrubs to screen and enhance the structures. Wherever possible, they will be continuous with nearby street trees and amenity plantings.

 

With the incorporation of mitigation measures, it is concluded that the landscape and visual impacts for both Designated and Non-Designated Elements will be acceptable.

 

18.8      Cultural Heritage Impact

18.8.1   Archaeology

The assessment has concluded that the construction of the proposed works would not have adverse archaeological impact provided that the following mitigation recommendations are implemented:

1.       Pre-testing is required at the following locations:

·     Mong Tseng Tsuen PS (non-designated element).  The pre-testing should comprise of the hand excavation of a minimum of one test pit measuring no less than 2 by 2 meters; and

·     Sewer alignment north of Tung Tau Tsuen (non-designated element).  The pre-testing should comprise of a field investigation with a minimum of 20 auger hole tests and hand excavation of two test pits measuring no less than 2 by 2 meters.

 

Pre-testing should be undertaken prior to construction, but after land resumption at Mong Tseng and north of Tung Tau Tsuen and surface removal of concrete and asphalt at north of Tung Tau Tsuen.

 

2.       Archaeological monitoring is recommended at the sewer alignment around the historical village of Tai Tseng Ng Uk Tsuen, Tai Tseng Wai and Shing Uk Tsuen (non-designated element).  The archaeological evaluation and archaeological monitoring should be conducted by a qualified archaeologist, who should be licensed by the Antiquities Authority before the evaluation or archaeological monitoring takes place.

 

18.8.2   Built Heritage

Construction Phase

The following resources will require mitigation during the construction phase:

a) Lau Fau Shan to Mong Tseng

Lau Fau Shan Road  - Modern shrine AAHB-21: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works area by metal barriers.

 

b) San Tin to Ngau Tam Mei

Fan Tin Tsuen - Man Lun Fung Ancestral Hall AAHB-405: As the works are in close proximity to the southwestern wall of the ancestral hall, which is a Declared Monument, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended. The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

The colour treatment of the proposed pumping station at Fan Tin Tsuen (P4) should minimise visual impact. It is recommended in the detailed design stage that the design and materials of the proposed pumping station should visually harmonize with the existing historic ancestral halls of Man Lun Fung and Ming Yuen Tong, for example, grey brickwork and granite are preferable for the exterior elevations.

 

Shrine AAHB-419: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Ming Yuen Tong AAHB-433: As the works are in close proximity to the southeastern wall of the ancestral hall, which is a Grade II building, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended. The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

Shun Yue Tong (Grade II) and San Yeh Man Tong (Grade I) AAHB-486 and 487: As the works are in close proximity to the southeastern walls of both of the ancestral halls, the contractor must carry out a condition survey of both of the buildings. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended.  The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures.

 

c) Castle Peak Road

Castle Peak Road (Yau Mei Tsuen) - Shrine AAHB-242: The shrine is located at a sufficient distance as to not require any protective measures during the construction phase. Access from Castle Peak Road should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Temple and shrine AAHB 227: The temple, although renovated contains historical architectural elements and is located directly on the edge of the works area. Hence, the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended. The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures. The shrine is located at a sufficient distance as to not require any protective measures during the construction phase. Access to the temple and shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Modern Village Gates AAHB-231 and 240: The base of the gates should be provided with a protective covering in the form of heavy duty plastic sheeting, supported by scaffolding where necessary.

 

Castle Peak Road (Yau Mei Tsuen) - Shrine AAHB-242: The shrine is located at a sufficient distance as to not require any protective measures during the construction phase. Access from Castle Peak Road should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

d) Shap Pat Heung

Kung Um Road - Shrine AAHB-262: The shrine should be provided with a minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Tai Tong Road - Modern Village Gates AAHB-129, 131,153,162, 164 and 211: The base of the gates should be provided with a protective covering in the form of heavy duty plastic sheeting, supported by scaffolding where necessary.

 

Shrine AAHB-207: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Tai Shu Ha Road East - Shrine AAHB-224: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Temple AAHB-226: The entrance to the temple is located directly from Tai Shu Ha Road, access from the road should be maintained throughout the construction phase.

 

e) Yuen Long Effluent Pipeline

Shrine AAHB-357: The shrine should be provided with a buffer zone of minimum 1 m, marked out by high visibility fencing and access to the shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Operational phase

The following resources will require mitigation measures for the operational phase:

·     Lau Fau Shan to Mong Tseng: Village structures (AAHB-29 – 53) in Mong Tseng Tsuen

·     San Tin to Ngau Mei Tsuen: Man Lung Fung Ancestral Hall (AAHB-405) and Ming Yuen Tong (AAHB-433) in Fan Tin Tsuen

·     Tai Shu Ha Road: Temple (AAHB-226) in Tai Shu Ha Road East (Nga Yiu Tau)

 

The mitigation will consist of landscaping of the area around the pumping station should include planting of foliage complimentary to the existing environmental setting, in order to screen the proposed pumping station and minimise visual impacts. The colour treatment of the proposed pumping station should minimise visual impact.

 

With the incorporation of mitigation measures during construction and operating phases, adverse impact related to cultural heritage is not anticipated.

 

18.9      Fisheries Impact

Within the non Designated Elements, none of the sewer alignment or the pumping station locations would constitute permanent direct impacts to any Grade A active fishponds. Only a fraction (0.05 ha) of a Grade C fishpond in San Wai would be subject to direct loss. Potential impacts to fisheries resources and operations may arise from permanent loss of fishponds. Due to the small percentage compared to the overall resources in Hong Kong, permanent losses of fisheries resources due to the project are predicted to cause minimal impacts to HKSAR fisheries. The impact is minimal and acceptable.

 

Within the Designated Elements,a total area of 0.20 ha will be temporarily occupied at four Grade A fishponds (mainly earth bunds) at Shan Puiduring the construction phase. These fishponds will be reinstated after the construction works and thus the impact is minor and acceptable.

 

Indirect impacts might be caused by site runoff from the works areas. The impact is ranked as minor in nature. Good site practice would be sufficient to mitigate this potential impact.

 

18.10    Summary of Options Review

18.10.1Options Considered on Package Alignment (Designated Element)

For the design of the Yuen Long Effluent pipline, two alignment options have been reviewed:

·     Conforming Scheme of 2A-1T (Figure 1.4 & Figures 1.4.1 to 1.4.6) - The proposed works under the conforming scheme are divided into six works items.  The whole section is 7,350m long of twin rising mains of 1400mm in diameter.  Major parts of the sewage alignment (2,140m) and the Yuen Long Effluent Pumping Station will be located within the Deep Bay Buffer Zone, Wetland Conservation Area and Wetland Buffer Area.

·     Alternative Scheme of 2A-1T (Figure 1.1 & Figures 1.1.5 to 1.1.9) - The proposed works under the alternative scheme are divided into seven works items.  The whole section has been reduced to 6,990m long of twin rising mains of 1400mm in diameter.  Except for the small-scale Yuen Long Effluent Pumping Station (same SPS location as the Conforming Scheme) on a plantation area, the alignment will run away from the Deep Bay Buffer Zone and about 80% of the sewage alignment will be laid underneath existing and future roads.

 

Considerations have been given comprehensively (in Section 5) in order to identify the preferred alignment that would achieve an optimal balance between environmental, engineering, connectivity, work programme etc, in accordance with the latest available information.  It is concluded that the 2A-1T Conformign Scheme is a “No built” option while the 2A-1T is selected as the Preferred Option.

 

18.10.2Options Considered for Locatons of Yuen Long Effluent Pumping Station (AP1) and alignment within WCA (AS1) – Designated Element

For the selection of the Yuen Long Effluent pumping station, three alternative sites have been investigated in the vicinity of YLSTW (Appendix 5.1).  DSD has therefore conducted a detailed utility search, ground review and engineering investigations on the alternative sites and other nearby areas.  Judging from the respective pros and cons of the three options as well as the surrounding site conditions as mentioned above, Option 1 is the most preferable and viable site option for the YLEPS from engineering, environmental and land points of view.  Detailed engineering justifications, maintenance problems and supportive reasoning have been sent to relevant authorities to justify Option 1 (the current design) is the only feasible option.  Other options, including Options 2 and 3 are considered to be technically/engineering infeasible.

 

18.10.3Options Considered for Locations of San Lung Tsuen SPS (P4) – Non Designated Element

For the selection of the San Lung Tsuen pumping station (P4), DSD has conducted a detailed utility search, ground review and engineering investigations on the site. Geographical, topographical, hydraulic, engineering, environmental, land availability and maintenace aspects have been considered in details.  Two sites for the San Lung Tsuen SPS had been proposed by DSD for initial engineering consideration (Figure 5.1).  However, owing to the fact that the land is a private site and there is currently a new building development under construction, this proposal for alternative site had been discarded. No other vacant site can be found in the nearby area.  The current location has been selected and no adverse environmental impact is identified when mitigation measures are incorporated.

 

 


19.0      CONCLUSION

19.1      Air Quality

19.1.1   Construction Dust

Designated Elements and Non-designated Elements

With the implementation of proper contractual clauses and Best Site Practice controlled within the APC (Construction Dust) Regulation, adverse dust impact is not anticipated.  An effective EM&A system is proposed to ensure the dust impact during construction phase is controlled within the legislative criteria.

 

19.1.2   Odour Impact During Operational Phase

Designated Elements

Cumulative odour assessment has been conducted.  Best practical means and proper mitigation measures including effective ventilating system and odour removal filters have been proposed, and no adverse odour impact during operational phase would be anticipated. For YLEPS (AP1/OP1 of 2A-1T) and Ngau Tam Mei SPS (P1 of 2A-2T/2B-1T), a filter with H2S removal efficiency of not less than 99.5% has been recommended.

 

Non-designated Elements

An odour removal filter with the following H2S removal efficiency shall be provided:

·     of not less than 99.5% for P2 to P5 SPS of 2A-2T and 2B-1T.

·     of not less than 95% for all SPS at 2A-3T (A1 to A2); and

·     of not less than 95% for all SPS at 2B-2T (B1 to B7).

 

Best practical means and proper mitigation measures including effective ventilating system have been proposed such that no adverse odour impact during operational phase would be anticipated.

 

19.2      Noise

19.2.1   Construction Noise

Designated Elements and Non-Designated Elements

Concurrent construction noise impacts from both pumping station and sewers have been assessed. A theoretical worst case in construction noise assessment has been undertaken with the consideration of cumulative impacts arising from other projects proposed in the vicinity of the study area. Unmitigated construction noise would cause exceedance of the daytime construction noise criterion.

 

Mitigation measures such as adopting quiet plant, limiting the use of PME, using of temporary barriers along site boundary, and employing movable barrier close to construction plants for sewage pumping station construction have been recommended.  It is also recommended that sewers and the rising mains shall be constructed in segments of up to a maximum 50m in length at any one time in order to reduce the time of noise impact.

 

Due to the proximity of some NSRs to the works site, noise exceedances are predicted even with the adoption of the best practical mitigation measures for some isolated occasions. 

 

The exceedances are resulted from the construction activities along the pipework segment, which will have impact on the following NSRs at:

·     Tin Shui Wai Area (2A-1T): NT16 – 18, NT20 – 22, NT24, NT22a and NT24a. A maximum noise level of 85.9dB(A) is found at NT22a.

·     Ngau Tam Mei and San Tin Areas (2A-2T and 2B-1T): NN02, NN09, NN13-14, NN17, NN21- 22, NN24-27, NN43, NN45-47, NN50-52, NN19a and NN26a. With a maximum noise level of 89.4dB close to NN46-47.

·     San Lung Tsuen Area (2B-2T): NN31a, NN32-33, NN35-36, and NN38-40. Maximum noise level is 86.8dB at NN40.

·     Shap Pat Heung Area (2B-2T): NS01, NS11, NS13, NS16-17, NS24-28, NS31, NS34-36, NS40, NS42, NS45-48, NS51-57, NS59-61, NS64, NS66, NS68-70, NS72, NS19a&b, NS37a&b, NS39a, NS42a, NS49a, NS52a, NS70a, NS76 and NS76b. Maximum noise level is 89.4dB at NS66.

·     Lau Fau Shan Area (Alternative 2A-3T): NL13, NL22, NL29 and NP01. With a maximum noise level of 81.4dB at NP01.

 

The maximum predicted noise level will occur during road pavement and finish works, which is 19.4 dB (A) greater than the day-time noise criteria.  However, the period of such an exceedance is expected to last no more than 2 days.  For other construction activities, minor exceedance will be experienced for a period of 1-2 weeks on sewage laying works and half month on site preparation, respectively. The affected periods for each work packages and items have been detailed in Section 8.9. Also, a systematic event and action plan on noise impact should be undertaken as the core part of the EM&A programme in order to minimize the potential complaint.

 

It is recommended that regular monitoring of noise at NSRs as part of the EM&A programme will be required during the construction phase.

 

19.2.2   Operational Noise

Designated Elements

There is no NSR within 300m from the YLEPS (AP1/OP1), and noise impact is not anticipated. For pumping station at Ngau Tam Mei Pumping Station (P1), the nearest NSR is located at 52m away and the maximum allowable SWL at lourve has been established. 

 

Non-designated Elements

During the operational stage, noise impacts due to the proposed sewage pumping stations will not be anticipated provided that proper acoustic treatment, including silencer or acoustic louvre is incorporated. In addition, absorptive wall linings could also be used to further reduce the internal reverberant noise.  Basic building design such as to avoid any opening or louvres facing the nearest NSR should also be adopted.  Noise commissioning at the site boundary and louvers of the proposed SPS is recommended.

 

19.3      Water Quality Assessment

Designated and Non-designated Elements

The construction phase impacts include:

·     the potential impacts on inland water quality from the land based construction activities; and

·     the potential impacts on inland water quality from crossings of the local streams.

 

Potential impacts on surface water quality due to land based construction activities would primarily occur due to surface run-off and wastewater generation from within the construction sites, including sewage effluent from the workforce.  The potential impacts may be readily controlled by on-site mitigation measures, which were specified in detail. Pipe Jacking method will also be adopted in crossing the local stream in order to avoid adverse impact on water quality.

 

The operational phase impacts include:

·     The potential impacts on inland and marine water quality due to the connection of currently unsewered areas to the Yuen Long STW; and

·     The potential impacts on inland and marine water quality due to uncontrolled effluent discharges due to failure of pumping stations.

 

The water quality modelling result has been reviewed. After the commence of the project, there will be a decrease in the discharge of untreated sewage effluent to inland waterways through connection to the Yuen Long STW but an increase in the treated effluent flows from the Yuen Long STW.  The results of the water quality modelling also revealed that there would be improvements in marine water quality in the vicinity of the mouth of the Shan Pui River, where the Yuen Long STW discharges.  An assessment of the impacts of the Stage 1 works on inland water quality indicated that there would be a reduction in polluting discharges to the inland waterways.

 

Mitigation measures were recommended to reduce the risks of failure of pumping stations and to ensure that timely responses are initiated in cases of failure in order to prevent adverse impacts on water quality due to the discharge of untreated sewage effluent.

 

No monitoring of water quality would be required during either the construction or operational phases.  It was recommended that regular audits of the implementation of the specified mitigation measures be carried out during the construction of the Project.

 

19.4      Waste Management

Designated Elements and Non-designated Elements

The following quantities of waste are expected to arise during the construction of the proposed gravity sewer and pumping station: public fill of 111,460m3(46,168m3 from 3 work items of Designated Elements and 65,292m3 from 38 work items of Non-designated Elements under 4 packages); and chemical waste (less than hundred liters per month); and general refuse.

 

Screening, solid waste, silt and debris will arise from the operation of the proposed Pumping Stations. Approximately 14.5m3 per month of material will be generated from the pumping station. The impact of its disposal at landfill will be minimal. The generation of chemical wastes is expected to be very small and no adverse environmental impacts are envisaged.

 

Good waste management practices have been recommended to ensure that adverse environmental impacts from the handling and disposal of construction and operational wastes are prevented or minimized. It is concluded that no unacceptable environmental impacts will result from the construction and operation of the proposed sewerage and Pumping Stations.

 

19.5      Land Contamination Assessment

Designated Elements and Non-designated Elements

A number of potentially contaminated premises are located within 50m of the proposed alignment of the gravity sewer and the pumping station. These premises include vehicle and mechanic maintenance and repair yards; car dismantling and dumps yards; construction equipment storage yards; small scale metal scrap yards; plastic drum cleaning/recycling and un-licensed petroleum filling station. The review of the historical and current land use was undertaken using information from aerial photographs, site visits and government and public information on potential “hot spot” area.

 

The assessment results indicated that the overall contamination concerns to the Project site area are very low. It is considered that the preparation of the Contamination Assessment Plan (CAP) for the detail site investigation, is not required and not practical for the Project site, as the proposed sewer alignment and the location of pumping station do not lie within the potential contaminated premises.

 

Although the risk of land contamination of the Project site area is very low, it is still recommended to conduct a “Confirmation Soil Test” during the trench excavation to further safeguard the construction workers. The details of the Confirmatory Soil Test are stipulated in Section 12.6. In case of the excavated soils are confirmed as contaminated, the remediation method as stipulated in Section 12.7 will be adopted to remediate the contaminated soils before disposal.

 

19.6      Ecological Assessment

Most of the study area, particularly the area to be directly affected by the proposed Project is highly urbanised and degraded by existing and on-going development.  Habitats found within the study area include plantation, mixed woodland, grassland/shrubland, cultivated land/orchard, fishpond, stream/channel, mangrove, and disturbed/urbanized/wasteland areas.  Two species of plants and 4 species/groups of birds of conservation interest were recorded. 

 

Designated Elements

The designated elements would cause a permanent loss of 0. 39 ha of urbanized/disturbed/wasteland and 0.23ha of plantation for construction of pumping stations, and a temporary loss of 0.24 ha of urbanized/disturbed/wasteland and 0.20 ha of fishponds for construction of sewers.  There will be no-net-loss in wetland area at the WCA and CA. 

 

Non-designated Elements

The non-designated element would cause a permanent loss of 0.95 ha of urbanized/disturbed/wasteland, 0.05 ha of fishponds and 0.12 ha of cultivated land and a temporary loss of 25.49 ha of urbanized/disturbed/wasteland, 0.46 ha of mixed woodland, 0. 28 ha of shrubland/grassland, 0.02 ha of plantation and 0.14 ha of cultivated land.  The overall ecological impacts are ranked as minor.  Standard site practice and recommendations to each works package are made.  No residual impacts are anticipated.

 

19.7      Landscape & Visual Impact Assessment

Designated Elements

The following pumping stations are designated elements and are therefore, required to undertake the approved mitigation measures as stated in Section 14.9.1:

·     Yuen Long Effluent Pumping Station (Package 2A - 1T); and

·     Ngau Tam Mei Sewage Pumping Station (Package 2A - 2T).

 

For the designated elements, it is concluded that in accordance with the definitions in the EIAO Annex 10, the landscape and visual impacts will be acceptable with mitigation measures.

 

Non-designated Elements

For the non-designated elements, it is concluded that in accordance with the definitions in the EIAO Annex 10, the landscape and visual impacts will be acceptable with mitigation measures.

 

19.8      Archaeology Assessment

Designated Elements

No archaeological impacts will occur on Designated Elements. 

 

Non-designated Elements

·     Mong Tseng Tsuen PS

Further investigation should be carried out after the resumption of the land and prior to commencement of any works.  The investigation should comprise of a minimum of one test pit excavation, measuring no less than 2 by 2 meters to verify the stratigraphy and potential archaeological deposits in the Mong Tseng PPS.

 

·     Sewer alignment on Wang Chau

The results from the field investigation indicate a lack of archaeological deposits and cultural soils.  No further action is required.

 

·     Sewer alignment north of Tung Tau Tsuen

Investigation should be carried out after the resumption of the land and prior to commencement of any works.  The investigation should comprise a minimum of sewer alignment north of Tung Tau Tsuen (non-designated element).  The pre-testing should comprise a minimum of 20 auger hole tests and two test pit excavations measuring no less than 2 by 2 meters, to verify the stratigraphy and potential archaeological deposits within the known archaeological site. 

 

·     Shan Ha Tsuen SPS

The field investigation results indicate that the area exists of sterile alluvial deposits with a high water table and is thus considered to have no archaeological potential.  No further action is required.

 

·     Shung Ching San Tsuen SPS

The field investigation results indicate that the area has been artificially raised by 1.5m fill.  Sterile alluvial deposits were encountered at a depth of more than 1.5m. No further action is required.

 

·     Sewer alignment from YLEPS to Wang Chau

Archaeological monitoring is recommended during the excavations of the sewer alignment between the historic villages of Tai Tseng Ng Uk Tsuen, Tai Tseng Wai and Shing Uk Tsuen (Figure 15.48).

 

19.9      Built Heritage Assessment

19.9.1   Designated Elements and Non-Designated Elements

All impacts fall within non-designated elements of the project.

 

Built Features

 

Mitigation measures for the construction stage including condition surveys and the implementation of monitoring and precautionary measures for the following resources in Fan Tin Tsuen: Man Lun Fung Ancestral Hall (AAHB-405), Ming Yuen Tong (AAHB-433) and the Shun Yue Tong and San Yeh Man Tong AAHB-486 and 487.

 

Shrine AAHB-21 (Lau Fau Shan Road), Shrine AAHB-419 (Fan Tin Tsuen), Shrine AAHB-262 (Kung Um Road), Shrine AAHB-224 (Tai Shu Ha Road East), Shrine AAHB-207 (Tai Tong Road), Shrine AAHB-242 (Yau Mei Tsuen) and Shrine AAHB-357 (Fuk Shun Street): a buffer zone should be provided of minimum 1 m, marked out by high visibility fencing and access to the shrines should be maintained through the provision of walkways separated from the works area by metal barriers.

 

Temple AAHB-226: Access from Tai Shu Ha road should be maintained throughout the construction phase.

 

Temple and shrine AAHB 227: the contractor must carry out a condition survey of the building. This survey must be carried out in advance of works and a report must be compiled, containing description of the types of construction, identification of fragile elements, an appraisal of the condition and working methods for any proposed monitoring and precautionary measures that are recommended. The report must be submitted to AMO for approval before construction activities commence. Upon approval the contractor shall implement the approved monitoring and precautionary measures. The shrine is located at a sufficient distance as to not require any protective measures during the construction phase. Access to the temple and shrine should be maintained through the provision of walkways separated from the works areas by metal barriers.

 

Mitigation measures for the operational stage, including landscaping of the area around the pumping station by planting of foliage complimentary to the existing environmental setting, will be required by the following resources:

·     Lau Fau Shan to Mong Tseng: Village structures (AAHB-29 – 53) in Mong Tseng Tsuen

·     San Tin to Ngau Mei Tsuen: Man Lung Fung Ancestral Hall (AAHB-405) and Ming Yuen Tong (AAHB-433) in Fan Tin Tsuen

·     Tai Shu Ha Road: Temple (AAHB-226) in Tai Shu Ha Road East (Nga Yiu Tau)

 

 

Buddhist Blessing Stones

There will be no impacts to Buddhist blessing stones during either the construction or operational phases, therefore no mitigation measures will be necessary.

 

Graves

There will be no impacts to any of the surveyed graves in the study area or to those located within the Cassino camp during either the construction or operational phases, therefore no mitigation measures will be necessary.

 

Cultural and Historical Landscape Features

No cultural or historical landscape features will be impacted by the project during either the construction or operational phase, therefore, no mitigation measures will be required.

 

19.10    Fisheries Assessment

Designated Elements

0.2 ha of temporary fish pond loss (mainly earth bunds) would be caused by the Designated Elements of this project.  The fishpond areas will be reinstated after construction.

 

Indirect impacts might be caused by site runoff from the works areas. The impact is ranked as minor in nature. Good site practice would be sufficient to mitigate this potential impact.

 

Non-designated Elements

Though Grade A active fishponds were identified within the assessment area with the majority concentrated to the Shan Pui, Nam Sang Wai, Tai Sang Wai and San Tin, the majority of assessment area appears to be degraded through urbanisation and development. None of the sewer alignment or the pumping station locations would constitute permanent direct impacts to any Grade A active fishponds. Only a fraction (0.05 ha) of a Grade C fishpond in San Wai would be subject to direct loss. Potential impacts to fisheries resources and operations may arise from permanent loss of fishponds. Due to the small percentage compared to the overall resources in Hong Kong, permanent losses of fisheries resources due to the project are predicted to cause minimal impacts to HKSAR fisheries. The impact is minimal and acceptable.

 

A total area of 0.20 ha will be temporarily occupied at four Grade A fishponds (mainly earth bunds) at Shan Pui during the construction phase. These fishponds will be reinstated after the construction works and thus the impact is minor and acceptable.

 

Indirect impacts might be caused by site runoff from the works areas. The impact is ranked as minor in nature. Good site practice would be sufficient to mitigate this potential impact.

 

 


20.0      references

 

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[5]      Air Pollution Control (Construction Dust) Regulation, HKSAR

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