·
Lung Fu Road Slip Road:
a direct connection between existing Lung Fu Road (LFR) viaduct and Tsing Wun
Road (TWR) for both traffic directions. This slip road acts as a parallel route
of Tuen Mun Road (TMR), which can increase the attractiveness of the current
alternative route along Lung Mun Road (via Tsing Tin Road, Ming Kum Road, TWR)
to reach Tuen Mun Area 40 & Tuen Mun – Chek Lap Kok Tunnel (TM-CLKT);
·
Hoi Wing Road Slip
Road: a direct connection between Tuen Mun Road (Sam Shing Section) (TMR(SSS))
northbound to Castle Peak Road (Castle Peak Bay Section) (CPR(CPBS)) westbound
near Hoi Wing Road (HWR); and,
·
Widening of existing
Wong Chu Road Slip Road: provision of a 200m additional traffic lane at the
downstream section of the existing slip road from TMR southbound to Wong Chu
Road (WCR) westbound to allow dedicated traffic lane for traffic heading to
Tuen Mun West and Tuen Mun South; thus, minimizing weaving movement at
downstream section of the heavily trafficked slip road.
Scenarios |
Environmental Benefits |
Environmental Disbenefits |
With Project |
· Provide alternative route accessing LFR to/from TWR, and TMR heading to HWR, thereby relieving congestion and decreasing the impacts to air quality and noise along the existing WCR and TMR |
· C&D materials will be generated due to the excavation and lateral support works along TMR (potential for re-use and at other projects) · Construction phase environmental impacts such as construction noise, dust, site surface runoff etc. (implement good site practices) · The air quality and noise impact imposed on the Air Sensitive Receivers/ Noise Sensitive Receivers (ASRs/NSRs) close to the new slip roads may be increased. |
Without Project |
· No construction-related environmental impacts to TMR, LFR and TWR · No wastes generated
|
· Many of the existing road links are already operating close to or above capacity. Congestion, and therefore impacts to air quality and noise, of not only TMR, WCR, LFR and TWR, but also large areas in Tuen Mun and beyond will continue to worsen. |
·
Avoid noisy
construction activities during school examination period and schedule the
construction works in the vicinity of schools and kindergartens during summer
recess as much as possible if programme allows; and
·
Close liaison with the
contractors of other concurrent projects in order to avoid overlapping of
construction activities and allow sufficient buffer for works at project
interface due to potential delays in the programme so that the cumulative
effects of environmental impacts could be minimized.
Considerations |
Description |
Engineering Factors |
|
Interface with Existing / Planned Facilities |
Different options of the alignment would have different interface issues with the existing / planned facilities, such as Christian Service Jockey Club Lodge of Rising Sun, Lung Yat Estate, Nam Fung Industrial Centre (i.e. Land Lot No. TMTL 233) and the Kau Hui public housing site. An option with the least interfacing issues relating to these facilities should be considered as far as practicable to avoid potential programme implication, land acquisition and disturbances to the environment. |
Nature of the traffic/ Road Safety |
A number of factors determining traffic safety in both the design and construction of flyovers and associated road links include: - provision of sufficient diverging distance; - minimization of cross weaving issues; - achievement of a maximum vertical gradient of 8% - achievement of desirable minimum sightline |
Land issue |
Minimization/avoidance of land resumption and/or land clearance |
Slope Works |
Minimization of slope excavation works |
Construction Programme |
Minimisation of construction period. Shorter construction period is preferred to minimise the disturbance to the community. |
Constructability |
- Practicality in constructing the viaduct and abutment structures, and carrying out slope works in the well-developed area; and, - Difficulty in undertaking utilities diversion and Temporary Traffic Management Scheme
|
Environmental Factors |
|
Construction Dust |
Minimisation of construction dust impact |
Noise |
Minimisation of construction plant noise impacts |
Terrestrial Ecology |
Avoid direct impact and minimise disturbance to sensitive ecological area |
Water Quality |
Minimisation of construction activities which would affect water quality |
Cultural Heritage |
Minimisation of construction impacts and disturbance to the identified cultural heritage resources and built heritages |
Other Factors |
|
Community Disruption |
The construction works arising from the Project should be minimised as far as practicable to minimise the disturbance to the community. |
Hoi Wing Road Slip Road (HWRSR)
·
Option H1: to provide a
slip road from TMR(SSS) northbound to CPR(CPBS) westbound near HWR with an
exclusive left turn lane from HWRSR to junction of CPR(CPBS)/ HWR (see Figure 2.1a) ;
·
Option H2: to provide a
slip road from TMR(SSS) northbound to CPR(CPBS) westbound near HWR with
an exclusive left turn lane from HWRSR to junction of CPR(CPBS)/ HWR and
an underpass to divert traffic from CPR(CPBS) southbound (see Figure 2.1b); and
·
Option H3: to provide a
slip road from TMR(SSS) northbound to CPR(CPBS) westbound near HWR with
signalized junction at CPR(CPBS) (see Figure 2.1).
Table 2.3
Comparison of HWRSR Alignment Options
Considerations |
Option H1 |
Option H2 |
Option H3 (Preferred Option) |
Engineering Factors |
· Exclusive left turn lane from TMR(SSS) northbound such that traffic will be in free flow condition with no delay time · Intense cross weaving between traffic coming from CPR(CPBS) westbound and HWRSR causes potential road safety hazard · Lengthy construction period |
· Exclusive left turn lane from TMR(SSS) northbound such that traffic will be in free flow condition with no delay time · An underpass to divert existing CPR(CPBS) westbound traffic to avoid weaving issue with traffic from HWRSR · Require E&M maintenance due to the provision of barrier-free access (i.e. elevator) for pedestrian · No weaving issue concern · Longest construction period |
· Form a signalized junction at the intersection of HWRSR and CPR(CPBS) westbound which brings delay time to the traffic · Road gradient is slightly over the design requirements; however, it can be made good by providing addition traffic aids to notify drivers · No weaving issue concern · Shortest construction period |
Environmental Factors |
· Longer in length and relatively larger footprint · Generate relatively more C&D materials · Traffic queues induce air quality and noise impact · Higher air quality, noise, and landscape and visual impacts due to its proximity to residential buildings (e.g. Siu Lun Court and Hanford Garden), Sam Shing Temple and educational institutions · Less vehicle emission as no mandatory waiting time at signalized junction and gentler road gradient · Similar construction noise and dust issues · Affect the existing Arch to Sam Shing Temple · Affect a portion of the existing staircase to Sam Shing Temple · Relatively high cultural heritage impact due to the proximity to Sam Shing Temple which is sensitive to construction vibration, settlement and tilting · Affect the existing car park at the junction of CPR (CPBS)/ HWR |
· Relatively the largest footprint · Generate the most C&D materials due to the construction of extra underpass · Similar air quality, noise, landscape and visual impacts as Option H1 · Less vehicle emission as no mandatory waiting time at signalized junction and gentler road gradient · Similar construction noise and dust issues · Affect the existing Arch to Sam Shing Temple · Affect the entire existing staircase to Sam Shing Temple · Relatively high cultural heritage impact due to the proximity to Sam Shing Temple which is sensitive to construction vibration, settlement and tilting · Relatively the biggest impact to CEDD’s proposed cycle track |
· Relatively the smaller footprint · Generate relatively the least C&D materials · Relatively less landscape and visual impact as it is farther away from Sam Shing Temple · Relatively more vehicle emission during operation phase due to steeper road gradient and stopping at signalized junction · Similar construction noise and dust issues · Existing Arch to Sam Shing Temple can be retained · Only affect a small portion of existing staircase to Sam Shing Temple · The least cultural heritage impact as this alignment situates farthest away from Sam Shing Temple · The least impact to the existing car park |
Other Factors |
· Relatively shorter disruption to general public |
· Relatively longer disruption to general public |
· Relatively shorter disruption to general public |
·
Option LS1: to provide
a new viaduct connecting TWR southbound to existing LFR viaduct southbound, and
to shift the existing junction of TWR/ Yip Wong Road northward (see Figure 2.2a);
·
Option LS2: to provide
a new viaduct connecting TWR southbound to existing LFR viaduct southbound
without any junction modification (see Figure 2.2).
Table 2.4
Comparison of LFRSR – SB Alignment Options
Considerations |
Option LS1 |
Option LS2 (Preferred Option) |
Engineering Factors |
· Shifting of TWR/ Yip Wong Road (YWR) junction is required · Complicated traffic lane arrangement between LFRSR – SB and the existing road network · Do not require realigning existing slip road from TWR southbound to WCR eastbound · Meet merging distance design requirements · Steep road gradient with potential safety concern · Similar construction period · Clearance of existing dwellings/ squatter area near YWR is required · Require land resumption · Encroach into the boundary of Lung Yat Estate · Public objection is anticipated |
· Do not require to shift TWR/ YWR junction · Simpler traffic lane arrangement between LFRSR – SB and the existing road network · Require realignment of existing slip road from TWR southbound to WCR eastbound · Meet road gradient design requirement · Similar construction period · Do not require clearance of existing squatter area · No land resumption · Encroach relatively less into the boundary of Lung Yat Estate |
Environmental Factors |
· Generate the most C&D materials due to the modification of road junction and existing slope at YWR · Relatively higher construction noise and dust issues · Moderate landscape and visual impacts · Existing trees at the existing slope of YWR are affected · Higher vehicular emission due to steep road gradient · Similar air quality, noise, and landscape and visual impacts during operation |
· Generate relatively less C&D materials · Moderate construction noise and dust issues · Moderate landscape and visual impacts · No existing tree at the existing slope of YWR is affected · Less vehicular emission due to gentler road gradient · Similar air quality, noise, and landscape and visual impacts during operation |
Other Factors |
· Similar disruption period to general public |
· Similar disruption period to general public |
·
Option LN1: to provide
a new viaduct connecting existing LFR viaduct northbound to TWR northbound,
which the new viaduct will be connected to at-grade TWR near Light Rail (see Figure 2.3a);
·
Option LN2: to provide
a new viaduct connecting existing LFR viaduct northbound to TWR northbound,
which the new viaduct will be connected to a higher point of TWR(see Figure 2.3).
Table 2.5
Comparison of LFRSR – NB Alignment Options
Considerations |
Option LN1 |
Option LN2 (Preferred Option) |
Engineering Factors |
· Steeper road gradient · Longer extent of viaduct in proximity to the existing MTRCL Light Rail · Long construction period due to the extensive slopeworks near MTRCL Light Rail and complicated MTRCL advance protective works · Similar proximity to historic building (e.g. No. 3 San Shek Wan North Road) which are sensitive to construction vibration, settlement, and tilting |
· Meet road gradient design requirement · Relatively shorter extent and farther away from existing MTRCL Light Rail · Moderate construction period · Similar proximity to historic building (e.g. No. 3 San Shek Wan North Road) which are sensitive to construction vibration, settlement, and tilting |
Environmental Factors |
· High C&D materials generation · Similar construction noise and dust issues · Higher vehicular emission due to steep road gradient · Similar air quality, noise, and landscape and visual impacts |
· Relatively less C&D materials generation · Similar construction noise and dust issues · Less vehicular emission due to gentler road gradient · Similar air quality, noise, and landscape and visual impacts |
Other Factors |
· Relatively more disruption to general public due to proximity to Light Rail |
· Relatively less disruption to general public due to slightly away from Light Rail |
·
Construction of bridge
structure for LFRSR;
·
Construction of a
reinforced concrete “U-shaped“ trough and at-grade road for HWRSR.
Table
2.6 Engineering and
Environmental considerations for various construction methods for HWRSR
Considerations
|
Traditional Open Cut Excavation Method
|
Excavation and Lateral Support (ELS) Method
|
|
Sheet Piled Wall
|
Pipe Piled Wall
|
||
Engineering Factors
|
· Require extensive working space
· Require extensive road closure
· Bring the most traffic impact
· Best ability to overcome underground obstructions
· Require the least capacity of plants & equipment
· Longest construction period
|
· Moderate ability to overcome underground obstructions
· Require moderate capacity of plants & equipment
· Require moderate working space for plants & equipment
· Require moderate temporary traffic arrangement
· Relatively poor in ground settlement and seepage control
· Moderate construction period
|
· Good ability to overcome underground obstructions
· Require moderate capacity of plants & equipment
· Require moderate working space for plants & equipment
· Good in ground settlement and seepage control
· Moderate construction period
|
Environmental Factors
|
· Extensive felling of trees
· Excessive generation of C&D materials
· Moderate impacts on noise, vibration and air quality
· High impacts on water quality and landscape & visual
· Brings the most environmental impact due to longest duration of works
and largest works extent.
|
· Moderate felling of trees
· Moderate generation of C&D materials
· Relatively high impact on noise
· Low impacts on air quality, water quality, and landscape & visual
· Brings moderate environmental impact
|
· Moderate felling of trees
· Moderate generation of C&D materials
· Relatively less noise and vibration impact due to the available
non-percussive piling method
· Low impacts on air quality, water quality, and landscape & visual
· Brings moderate environmental impact
|
Table
2.7 Engineering and
Environmental considerations for various construction methods for LFRSR
Considerations
|
Precast Method
(E.g.: Launching girder/ Balanced Cantilever) |
Cast-in-Situ Method
|
|
Suspended Travelling Formworks
|
Ground-supported Falseworks
|
||
Engineering Factors
|
· Road closure required for each lifting operation due to road safety
concern and in close proximity of Light Rail
· Repositioning of plants & equipment involve temporary road closure
which would only be allowed during restricted hours
· Require the heaviest plants & equipment
· Require the longest time to set up heavy plants & equipment
· The longest construction period due to limited working space for
plants & equipment
|
· Works could be carried out during non-restricted hours as proposed
work would not take up carriageway space
· Require moderate capacity of plants & equipment
· Require the least working space for plants & equipment
· Road closure only required for repositioning of suspended travelling
formworks
· Moderate construction period
|
· Falseworks could be erected/ dismantled during non-restricted hours
· The most serious impact to existing traffic as road closure required
for all works over carriageway
· Require moderate working space
· Require the least capacity of plants & equipment
· Require the least setting up time for plants & equipment
· Shortest construction period as multiple works front could be set up
concurrently
|
Environmental Factors
|
· The worst night-time construction noise impact amongst all methods due
to heavy lifting operations during restricted hours
· The least amount of construction site activities & traffic flow
induced due to precast segmental construction
· Brings the most serious environmental impact in terms of the longest
duration of works
|
· Night-time construction noise impact due to repositioning the suspended
travelling formworks above existing carriageways not as serious as precast
method
· The largest amount of construction site activities & traffic flow
induced due to small scale cast-in-situ works for segmental construction
· Brings moderate environmental impact in terms of the moderate duration
of works
|
· Night-time construction noise impact due to erection of temporary
cross beams above existing carriageways not as serious as precast method
· Moderate amount of construction site activities & traffic flow
induced due to synergy of larger scale of cast-in-situ works
· Brings the least environmental impact in terms of the shortest
duration of works
|
·
Site Formation and Infrastructure
Works for Public Housing Developments at Tuen Mun Central – Phase 1;
·
Construction of Public
Housing Development (PHD) at Yip Wong Road Phase 1 and Phase 2;
·
Cycle track between
Tsuen Wan and Tuen Mun (Tuen Mun to So Kwun Wat Section);
·
Tuen Mun South
Extension;
·
Tuen Mun Bypass;
·
Reprovision of Tuen Mun
Swimming Pool, Tuen Mun Golf Centre Practice Green, Pet Garden and Community
Green Station; and,
·
Sports Ground and Open
Space in Area 16, Tuen Mun.
Table 2.8
Summary of Concurrent Projects
Project [Project Proponent] |
Construction Programme |
Potential Cumulative Impact |
||
Start |
Complete |
Construction Phase |
Operation Phase |
|
Site Formation and Infrastructure Works for Public Housing Developments at Tuen Mun Central – Phase 1 [CEDD] [1] |
2021 |
Q3/2024 |
Cumulative construction dust is not anticipated as heavy construction works of this concurrent project would be completed before commencement of the Project.
Cumulative noise impact was evaluated in Section 4 of this EIA Report. |
Not anticipated in view of the nature of the concurrent project. |
Construction of Public Housing Development (PHD) at Yip Wong Road Phase 1 and Phase 2 [HD] [2] |
2020 |
2024-2025 |
Cumulative dust and noise impacts were evaluated in Section 3 and 4 of this EIA Report respectively. |
Not anticipated in view of the nature of the concurrent project. |
Cycle track between Tsuen Wan and Tuen Mun [CEDD] [3] |
2023 |
2026 |
Cumulative dust and noise impacts were evaluated in Section 3 and 4 of this EIA Report respectively. |
Not anticipated in view of the nature of the concurrent project. |
Tuen Mun South Extension [MTRCL] [4] |
2023 |
2030 |
Cumulative dust and noise impacts were evaluated in Section 3 and 4 of this EIA Report respectively. |
Not anticipated in view of the nature of the concurrent project. |
Tuen Mun Bypass Project [HyD] |
2026 |
2033 |
Cumulative dust and noise impacts were evaluated in Section 3 and 4 of this EIA Report respectively. |
Cumulative air quality and noise impacts were evaluated in Section 3 and Section 4 of this EIA Report respectively. Due to considerable separation distance between the Project and this concurrent project, the cumulative impact is anticipated to be insignificant. |
Reprovision of Tuen Mun Swimming Pool, Tuen Mun Golf Centre Practice Green, Pet Garden and Community Green Station [MTRCL] [4] |
2023 |
2030 |
Cumulative dust and noise impacts were evaluated in Section 3 and 4 of this EIA Report respectively. |
Not anticipated in view of the nature of the concurrent project. |
Sports Ground and Open Space in Area 16, Tuen Mun [ArchSD] [5] |
2023-2024 |
2027-2028 |
Not Anticipated due to considerable separation distance between the Project and this concurrent project. |
Not anticipated in view of the nature of the concurrent project. |
Note:
[1]
Source: PWSC Paper at https://www.legco.gov.hk/yr20-21/english/fc/pwsc/papers/p20-18e.pdf
[2] Source: LegCo Paper at https://www.legco.gov.hk/yr2022/english/panels/hg/papers/hg20220207cb1-33-1-e.pdf
[3]
Source: EIA report at https://www.epd.gov.hk/eia/register/report/eiareport/eia_2802022/CONTENT%20PAGE.htm
[4] Source: EPD’s
website at https://www.epd.gov.hk/eia/register/profile/latest/esb332/esb332.pdf
[5] Source: ArchSD’s
webpage at https://www.archsd.gov.hk/en/projects/capital-projects-under-detail/278RS.html
Table
2.9 Summary of Concerns Raised
by TMDC T&TC Members and Follow Up Actions
Concerns / Issues |
Follow Up Actions to be Taken |
· Concerns of future logistics centres in Tuen Mun Areas 38, 40 and 46 would make WCR and HWR much busier |
· This EIA report is to address the environmental impacts. Details of the mitigation measures to be adopted during the construction and operational phases are discussed in the relevant chapters of this EIA report. |
· The commissioning of TM-CLKT will increase the traffic loading of Tuen Mun Road (Town Center Section), WCR and LMR |
|
· More congested traffic on TWR causing noise problem |
[1] : The original target commissioning
year of TMB was in 2036. Subsequently, the Government stated in the LegCo
meeting that they would strive to commission TMB in an earlier year (likely
2033).
[2] : Traffic flows in 2031 are extracted from traffic model. Traffic flows
in 2033 and 2036 before the commissioning of TMB are estimated by using the
growth rate method approved by the Transport Department. Traffic flows between
2031 and 2036 are obtained by applying corresponding growth rate (with an
agreed annual growth rate of 0.5%) to the modelled traffic flow in year 2031.
Traffic flows in 2036 and 2046 with TMB are extracted from traffic model.
between 2031 and 2036 are obtained by applying corresponding growth rate (with
an agreed annual growth rate of 0.5%) to the modelled traffic flow in year
2031. Traffic flows in 2036 and 2046 with TMB are extracted from traffic model.