| 10. The
Chairman said that Members appreciated the constraints of
site selection but it was the concern of the Subcommittee that
environmental aspects should be taken into account when selecting
the site. He asked the proponent to provide more details of
the site selection, in particular, environmental considerations.
11.
A Member said that the Authority should review whether
such kind of projects should be categorized as designated
projects because the environmental impacts could be substantial.
Another Member wondered why the project, being part
of the Disney project, was not a designated project in itself.
In reply, AD(EA)/EPD said that there were two types
of designated projects, one was under Schedule 2 of the EIAO
which required an environmental permit for construction and
the other was under Schedule 3 which dealt with development
feasibility study. The Disney project was a Schedule 3 project
and the reservoir was an individual project under the Northshore
Lantau Development which however did not fall under Schedule
2.
12. A
Member asked whether the reservoir could be located closer
to Disney Land. Atg. SE(Design)/WSD replied that the
location was so chosen in order to serve also the North Lantau
Development area.
Measures
to control construction site run-off
13. On
the Chairman's enquiry, Atg. SE(Design)/WSD said that
they would follow EPD's standard environmental pollution control
clauses in the works contract. But it was envisaged that the
site run-off at the initial stage of the construction would
not be a concern because works would commence in early October
2001 when the dry season began. By the time the wet season
started, the site drainage system would be in place to carry
surface run-off from torrential rainfalls. During the construction
stage, full-time professional and technical staff from WSD
would station on site to supervise the work of the contractor.
14. Since
Members did not have the control clauses at hand, the Chairman
asked the proponent to briefly explain what measures the contractor
would adopt to control site run-off. Atg. SE(Design)/WSD
said that the contractor would build a temporary drainage
line to collect the run-off to a designated location for de-silting
before discharge. In addition, a permanent washout pipe would
be constructed to collect all washed water arising from the
cleansing of the proposed service reservoir for discharge
into existing drainage culvert instead of stream courses.
15. A
Member asked if there would be a second access road during
construction or the same access road would be used for construction
and maintenance. Atg. SE(Design)/WSD said that the
same access road would be used for both purposes. That
Member then asked why the 1.1km long access road looked
much longer in the diagram than the 500m long pipelines. Atg.
SE(Design)/WSD explained that it was the visual perception
due to sloping angle.
16. A
Member was concern why a 60m-wide work site was needed
for a 3.5m-wide access road. SLA/HyD said that since
a lot of slope works would be involved and adequate surface
was needed to ensure effective mitigation planting on the
slope, the 60m-wide work site was a conservative estimation
of the area needed. Atg. SE(Design)/WSD supplemented
that 60m was just a maximum estimate. The actual area would
depend on the slope angle.
17. In
response to a Member's enquiry, SLA/HyD said that the
construction of the access road would not leave a landscape
scar because the slope would be completely re-vegetated. However,
she reminded Members that it would take 5 to 10 years for
the re-vegetated planting to grow for effective screening.
18. A
Member encouraged the proponent to use the species in
Annex B of AFCD's reply dated 15 December 2000 which were
proved to be more successful for re-vegetation. SLA/HyD
said that a tree survey had just been completed and they would
look for the species mix most suitable for the site. 19. The
Chairman concluded that the proponent should pay particular
attention to site run-off control and monitoring and re-vegetation
to minimize environmental impacts.
20. A
Member asked whether EPD would consider categorizing the
construction of fresh water service reservoir as a designated
project under Schedule 2 of the EIAO having regard to its
large footprint which could have substantial impact on the
environment. In response, AD(EA)/EPD said that Schedule
2 already covered a wide range of projects and compared with
those, construction of a reservoir would be a minor project.
Given existing resources, AD(EA)/EPD considered that
the possibility of adding more project types to the list under
Schedule 2 was quite remote.
Agenda
Item 5 : Monthly Update of Applications under the EIA Ordinance
21. Members
noted the monthly update of applications under the EIAO, the
tentative schedule for submission to ACE EIA Subcommittee,
and the lists for designated/non-designated projects not selected
for submission (as at 25 November 2000).
Agenda
Item 6 : Any Other Business
EM&A
of Penny's Bay Reclamation Project
22. At
the request of the Chairman, Consultant/MAL briefed
Members on the progress works undertaken in Penny's Bay, the
organization of environmental management and the impact on
water quality in relation to Ma Wan fish culture zone.
23. In
respect of works carrying out in Penny's Bay, Consultant/MAL
said that it involved dredging of uncontaminated mud at Penny's
Bay and disposal at the designated marine dumping sites as
controlled by the conditions set out in the environmental
permit. As regards the environmental management team, it was
employed by the contractor and was responsible for environmental
monitoring. The monitoring was supervised by Engineer's Representative
and Mouchel acted as the Independent Checker to countercheck
the monitoring data in accordance with the requirements set
out in the environmental permit, EIAO and EM&A Manual.
On water quality within Penny's Bay area, sensitive receiver's
stations were set up at Kau Yi Chau, Ma Wan, and Discovery
Bay; control stations were set up outside the range of impacts
as predicted in the EIA report; gradient stations were set
up between the works area and the sensitive receiver's stations.
On water quality at East Lamma Channel, more sensitive receiver's
stations, control stations and two stations were set up for
24-hour monitoring. All the monitoring data was made available
for the public on the Penny's Bay website. Consultant/MAL
said that significant increase in the amount of suspended
solid (SS) had been detected within the site of the Penny's
Bay works boundary and immediately outside the boundary. After
the alleged fish kills, additional monitoring stations had
been put between Penny's Bay and Cheung Sha Wan. However,
no impact on the fish culture zone was recorded other than
that predicted in the EIA report. After careful investigation
by Mouchel and AFCD, it was concluded that the fish kills
at Ma Wan and Cheung Sha Wan were not linked with Penny's
Bay reclamation works. The contractor had nevertheless made
an effort to minimize impact by putting in a silt curtain
to isolate the works area and the Discovery Bay.
24. Noting
that AFCD had conducted investigations into the alleged fish
kills, the Chairman enquired about the findings. FO/AFCD
said that fish samples from Ma Wan Fish Culture Zone were
taken for analysis. It was found that the fish suffered from
infection by bacteria and parasites and so far they were unable
to find any evidence relating the fish kill to Penny's Bay
reclamation works.
25. A
Member noticed that the fishermen in Ma Wan had been granted
ex-gratia allowance, he enquired about the criteria for granting
such allowance. He also said that Friends of the Earth had
carried out an independent one-day water sampling at Ma Wan
and found that the level of SS was 65 mg/L, which was much
higher than the worst case scenario of 39 mg/L predicted in
the EIA report. FO/AFCD said that AFCD recorded on
15 September 2000 a SS level of 72 mg/L at Ma Wan fish culture
zone. As for the criteria for granting ex-gratia allowance
to mariculturists, they were as follows-
- when
the SS level reached 100% of the average SS level over the
past 5 years; or
- when
SS level reached 50 mg/L; or
- when
dredging or dumping in marine borrow area or dumping ground
was carried out within 5km from a fish culture zone (approved
by the Finance Committee of the Legislative Council on December
1, 2000 with retrospective effect from March 15, 2000).
26. A
Member followed up by asking how frequent the SS level exceeded
39 mg/L, i.e. the worst-case scenario predicted in the EIA
report and what the average SS level was. Consultant/MAL said
that it was a complicated question and he passed on to Members
copies of the data from SR-7 which was the monitoring station
at Ma Wan fish culture zone.
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