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(ACE
Paper 28/2002)
For advice
INTRODUCTION
At
its meeting held on 5 August 2002, the Subcommittee considered
the environmental impact assessment (EIA) report on Deep Bay
Link (DBL).
ADVICE
SOUGHT
2.
Members are requested to advise whether the EIA report should
be endorsed.
VIEWS
OF THE SUBCOMMITTEE
EIA
report on Deep Bay Link
(ACE-EIA Paper 14/2002)
Need
for the project
3.
The Hong Kong Special Administrative Region and the Shenzhen
government proposed to provide a fourth vehicular boundary
crossing which is now known as the Shenzhen Western Corridor
(SWC) to meet the present and expected future traffic demand
between the two areas. DBL will serve as the strategic highway
linking SWC to Hong Kong's highway network.
Description
of the project
4.
DBL is a 5.4 km long dual 3-lane carriageway connecting SWC
at Ngau Hom Shek to the Yuen Long Highway at Lam Tei where
traffic could gain access to the road network including Route
3 Country Park Section to the east and Tuen Mun Road to the
west. It will also provide access to Ha Tsuen and the proposed
Hung Shui Kiu New Town.
Views
and recommendations of EIA Subcommittee
5.
Members' concerns on the project related mainly to the submission
of the EIA report of the project in isolation of the SWC project;
air quality impact during operational stage; relationship
between Air Quality objectives (AQOs) and impact on health;
cumulative impact of future road networks; cumulative impact
on Ramsar site; loss of egretry at Ngau Hom Shek; loss of
fishponds; residual traffic noise impact during construction
stage; visual impact of noise barriers during operational
stage and planting of native species of trees.
Why
the EIA reports of DBL and SWC were not submitted together
6.
Members queried why the EIA report of DBL and SWC were not
submitted together given that the two projects were directly
linked. There were concerns that in the absence of an EIA
on SWC, the endorsement of the DBL project would pre-empt
Members' acceptance of the landing point of SWC at Ngau Hom
Shek. Also, separate submission of the EIA reports of the
two projects would deprive Members' of the opportunity to
consider the overall cumulative impacts of the two projects.
The project proponent explained that due to the high urgency
of the DBL project, it was necessary to start related preparatory
work earlier. The landing point at Ngau Hom Shek had been
assessed during the Crosslink Further study and discussed
with Members several months ago during an informal dialogue.
As for cumulative impacts, Table 7.31 of Volume 1 of the EIA
report had listed out projects which together with DBL may
produce cumulative effects and also the details of the potential
cumulative impacts within the area of the current project.
Air
quality impact during operational stage
7.
On air quality impact during operational phase, the project
proponent team pointed out that air sensitive receivers within
500m from the project boundary would not be subject to any
exceedance in AQOs during the operational phase. The assessment
was based on a conservative assumption that all cross boundary
vehicles on the road network would use fuel with higher sulphur
content. Another conservative assumption adopted was the emission
factors in the year 2011 in designing the traffic flow in
2021.
Relationship
between AQOs and impact on health
8.
Some Members commented that AQOs was a crude and unreliable
indicator as far as health was concerned. Even though the
project complied with AQOs during the construction and the
operational stage, it did not necessarily mean that it would
not have any adverse impact on health. That said, Members
were aware that under the Technical Memorandum, the criteria
for evaluating air quality was meeting AQOs established under
the Air Pollution Control Ordinance. Unless there is a change
in policy, projects meeting the AQOs should not be challenged
as not being up to the required air quality standard.
Cumulative
impact of future road network
9.
On the cumulative impact of related road network on air quality,
the project proponent team pointed out that the air quality
modeling had taken into account the impact of Deep Bay Link
as well as other future road network. .
Cumulative
impact on Ramsar site
10.
On cumulative impact relating to disturbance, particularly
on Ramsar site, the project proponent team explained that
it was outside the works area of this EIA but the implications
would be assessed in greater details in the SWC project.
Loss
of egretry at Ngau Hom Shek
11.
Members were concerned that no compensation was provided for
the loss of breeding habitat for herons and egrets at Ngau
Hom Shek during the construction stage of the project. The
project proponent pointed out that the loss of the Ngau Hom
Shek egretry was considered minor in territory-wide terms
because of the small number of nests involved and the mobility
of the Ngau Hom Shek egretry. Alternative nesting locations
would also be available in nearby areas.
Loss
of fishpond
12.
Members were also concerned that during the construction stage
no compensation was provided for the temporary loss of 0.73
ha of fishponds that acted as feeding ground for birds. The
project proponent as well as AFCD officers pointed out that
based on information available, the two affected fishponds
had very low ecological value and one of them was an abandoned
and dried up fishpond. The major species identified near the
area of the two fishponds were a few Chinese Pond Heron and
Little Egret which were tolerant to disturbance. Alternative
feeding locations would also be available in nearby areas.
Therefore, compensation during the construction phase was
not necessary. Compensation in the long term would be provided
nevertheless. Individual Members had doubt about the approach.
Residual
construction noise impact
13.
Members expressed concern about residual noise impact of 4
dB expected at six dwellings at Tsoi Yuen Tsuen for a period
of about five weeks during construction phase. They noted
that under existing guidelines, the six dwellings would not
be qualified for the provision of air-conditioning.
Visual
impact of noise barriers during operational stage
14.
Members commented that the project proponent should avoid
using bright and conspicuous colour scheme for noise barriers
such as that adopted for the noise barriers in Tolo Highway.
Planting
of native species of trees
15.
Noting that about 6,500 trees would be planted as compensation
measures, Members suggested that native species of trees should
be given higher priority.
Conclusion
16.
After detailed discussion, the Subcommittee concluded that
it would recommend the EIA report to the Council for endorsement
with the following proposed conditions-
- the
project proponent should not commence work until the EIA
report of the SWC project is endorsed by the Council;
- the
project proponent should provide on-site or off-site compensation
for the loss of 0.73 ha of fishpond during the construction
stage or advance the section of work near pond no. 24 ahead
of other sections so that the proposed fishpond could be
created earlier to provide compensation;
- the
project proponent should ensure that the functions of the
recreated wetland adjacent to pond no. 24 are maintained
all year round;
- the
project proponent should consider providing alternative
accommodation during the impact period for the residents
of the six dwellings which are subject to residual noise
impact;
- the
project proponent should transplant mature trees, minimize
the number of trees to be felled, and select native species
of trees for planting;
- the
project proponent should avoid using bright and conspicuous
colour scheme for noise barriers such as that adopted for
noise barriers in the Tolo Highway;
- the
Habitat Management Plan should be approved by the authority
before implementation; and
- the
project proponent should provide data on background air
pollutant concentrations and the concentrations after the
completion of the project as generated from the modeling
for the EIA Subcommittee's reference.
EIA
Subcommittee Secretariat
August 2002
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