Agenda Item 1 : Confirmation of Minutes of 59th Meeting
held on 4 June 2001 The
minutes were confirmed subject to a Member's amendments.
Agenda
Item 2 : Matters Arising
Para.
18 : Selection of EIA reports
2. Members
noted that to facilitate their selection of EIA reports for
consideration in the future, EPD would attach to the list
for selection a copy of an extract of the project profiles
showing the purpose and nature, location and scale of the
projects.
Agenda
Item 3 : Strategic Assessment and Site Selection Study for
Contaminated Mud Disposal
(ACE-EIA Paper 4/2001)
3. The
Chairman welcomed CGE(FM)/CED, SGE(MD)/CED and ED/ERM
to the meeting. CGE(FM)/CED then introduced the background
of the Study followed by ED/ERM's presentation of the detailed
findings and recommendations.
4. In
response to the Chairman's question, CGE(FM)/CED confirmed
that the purpose of this briefing was to seek the Subcommittee's
view on the proposed preferred site for Contained Aquatic
Disposal (CAD) facility as an intermediate contaminated mud
disposal facility for the period from 2007 to 2010. The project
proponent would commission an EIA study to ascertain the environmental
acceptability of the preferred site and disposal option.
Contaminated
Mud Disposal Policy
5. The
Chairman asked apart from a contaminated mud disposal
strategy, whether the Government had a contaminated mud management
strategy in place and if yes, what steps had been taken to
implement the strategy. In reply, CGE(FM)/CED said
that it was the Government's policy to minimize mud arising
by vetting the applications from project proponents for an
allocation of mud disposal capacity. An allocation would only
be granted with full justification on why dredging was unavoidable,
for example, maintenance dredging. He added that the relevant
Works Bureau Technical Circular was being revised with a view
to further reducing mud arising.
6. In
response to the Chairman's follow up question, CGE(FM)/CED
said that about half of the total contaminated mud arising
was contributed from unavoidable dredging.
7. A
Member queried the need for an intermediate CAD facility
whereas a Confined Disposal Facility (CDF) seemed to be a
longer-term solution. She was concerned that without a long-term
strategy, more CAD facility might be built in a piece-meal
basis to cater for mud arising beyond 2010. CGE(FM)/CED
explained that given that public works such as a CAD facility
would take five years from planning to implementation, it
was considered the right time to plan for it to meet anticipated
demand in 2007. Although a CDF might serve as a long-term
solution, CAD provided greater flexibility for capacity expansion
or contraction to cater for the uncertainty of the amount
of mud arising in the following years due to changes in mud
classification system. The Administration had just commissioned
a consultancy study, expected to complete by 2002, to explore
CDF and co-disposal of public filling materials and dredged
materials.
8. A
Member asked whether other options like disposal in landfills
would be more cost-effective if the amount of mud arising
was considerably less than expected. ED/ERM replied
that upland disposal options had been looked at and the detailed
results were contained in Report on Assessment of Disposal
Options. In a nutshell, upland disposal options incurred higher
costs due to scarcity of land and were usually implemented
in situations where other options were not available.
9. The
Chairman asked whether it was true that CAD was not a
preferred contaminated mud disposal option in other countries.
In response, ED/ERM said that this option was widely
adopted in United States.
10. A
Member said that according to his understanding the United
States would ensure that mud was treated to the level suitable
to be disposed at CAD facilities. He asked about the level
of contamination of mud classified to be disposed at the proposed
CAD facility in Hong Kong. ED/ERM said that the proposed
CAD facility was designed for Type 2 disposal whereas only
Type 3 dredged materials required special treatment.
11. On
that Member's follow up question, CGE(FM)/CED said
that Hong Kong had not yet identified any Type 3 dredged materials
through biological screening.
12. That
Member said that a study conducted by Parson & Jefferson
concluded that untreated sewage discharged into Hong Kong
waters contained anthropogenic toxic substances which were
harmful to Chinese White Dolphins. He asked whether the Government
would in the future prohibit dredged materials containing
toxic substance to be disposed in Hong Kong waters. CGE(FM)/CED
said that Hong Kong followed the stringent requirements of
the London Convention in which disposal of materials containing
insignificant amount of toxic substance in the sea was allowed.
Assessment
Criteria
13. The
Chairman asked why the criteria used in the suitability
assessment of alternative disposal options did not include
sustainability. In reply, CGE(FM)/CED said that CAD
was considered sustainable because when the seabed pit was
filled and capped with uncontaminated material, the original
seabed level would be restored. The Chairman however
pointed out that it was unsustainable from the point of view
that the site could not be re-used. ED/ERM responded
that sustainability relied on minimizing dredged materials
requiring disposal. Sustainability should also be considered
at a territory-wide level. For example, building a submarine
railway tunnel would on the one hand generate dredged materials
but on the other hand reduce vehicle emissions and noise on
roads.
Airport
East CAD vs East Sha Chau CAD
14. In
response to a Member's question, ED/ERM said that Airport
East rather than East Sha Chau was preferred because more
activities of the Indo-pacific Humpbacked Dolphin were recorded
within the areas of the latter site. East Sha Chau was also
in close proximity to Sha Chau, Lung Kwu Chau Marine Parks
and it impinged upon the Jet Foil runway. CGE(FM)/CED
supplemented that Airport East was more favorable because
the water was shallower.
15. On
that Member's follow up question, CGE(FM)/CED said
according to whole body analysis of fish, there was at present
no indication of greater health risk to the dolphins in East
Sha Chau area than elsewhere but there was still risk potential.
Another Member said that the threat posed by certain
chemicals to the health of dolphins was established in the
study conducted by Parson & Jefferson which showed that
the bodies of 64 dolphins examined contained anthropogenic
toxins. However, CGE(FM)/CED responded that there was
no evidence to show that there was a causal relationship between
contaminated mud disposal activities and health conditions
of the dolphins. That said, they would recommend Airport East
to because it would reduce the potential risk. AD(Cons)/AFCD
supported the preference of Airport East to East Sha Chau.
16. A
Member noted that it was scientifically difficult to establish
a causal relationship between mud disposal activity and dolphin
population but it was not necessarily true that there were
no adverse impacts on the dolphins. A recent survey conducted
by the World Wide Fund For Nature Hong Kong showed that there
were increasing dolphin activities in the Airport East area
because marine traffic was restricted in the Airport Exclusion
Zone. She urged the proponent to take a cautious approach.
17. A
Member pointed out that Siu Ho Wan Sewage Treatment Works
would soon commence operation, the EIA study of Airport East
or East Sha Chau should take into account sewage discharge
from that treatment plant. CGE(FM)/CED said that all
cumulative impacts would be taken into consideration in the
EIA study.
18. A
Member was concerned that the traffic of barges carrying
mud arising would create disturbance to the dolphins. ED/ERM
assured him that the route of the barges would be considered
in detail under the EIA study. CGE(FM)/CED supplemented that
the impacts, if any, caused by the barges would be insignificant
due to their low speed.
19. A
Member was of the view that the East Sha Chau option should
be subject to EIA study apart from the Airport East option
unless the proponent had evidence to prove that there would
be detrimental impacts to dolphins in East Sha Chau area.
20. A
Member considered that if the proponent were to confine
the EIA study to the Airport East option, they would have
to bear the risk of finding that the site was unsuitable for
CAD facility due to insurmountable cumulative impacts from
sewage discharge by Siu Ho Wan Sewage Treatment Works. In
response, ED/ERM said that the impacts of sewage discharge
would depend on the location of the outfall.
21. On
ED/ERM's question, AD(EA)/EPD said that the project
profile would be exhibited under the EIA Ordinance and ACE
could comment on it before EPD issued the Study Brief. He
said that if Members considered that the EIA study should
cover more options that just the Airport East CAD option,
the authority would take such comments into account when drawing
up the study brief. CGE(FM)/CED said that they welcomed
as much inputs and comments at this stage from the Subcommittee.
22. A
Member said that the CAD option at Airport East was not
a non-starter. That said, he felt that the Administration
could work out a high growth and a low growth scenario in
forecasting the amount of contaminated mud arising after 2010
to speed up future determination of a long-term strategy for
disposal of contaminated mud.
23. A
Member was not convinced that the proposed facility was
a sustainable solution to contaminated mud disposal and hoped
that the proponent would re-consider the option of CDF. She
recommended referring the issue to the full Council for further
discussion. Three other Members supported that Member's
recommendation.
24. Members
reckoned that there was no ground to advise the proponent
not to proceed with an EIA study on the Airport East CAD option,
bearing in mind that the proponent would bear the risk of
commissioning another EIA study should the Airport East CAD
option was found unsuitable at the end of the day.
25. The
Chairman concluded that the Subcommittee was concerned
over the long-term strategy/policy on contaminated mud disposal
and management, and noted that a consultancy study was commissioned
to address this concern and to consider options including
CDF. The Subcommittee was not in a position to endorse the
proposed site and option for the intermediate contaminated
mud disposal facility due to lack of assessment details. Nonetheless,
Members noted that proponent's point that CDF was not a sensible
option for an intermediate measure as it was desirable neither
in financial nor in planning terms. They suggested the project
proponent to consider more options other than the Airport
East CAD option and that cumulative impacts, in particular
sewage discharged from Siu Ho Wan Sewage Treatment Works,
should be included in the EIA study. As agreed, the Subcommittee
would refer the paper to the next Council meeting for consideration
and invite the proponent to attend the meeting. A Member
suggested the proponent to consider inviting representatives
from Works Bureau which was responsible for the long-term
contaminated mud disposal/management strategy.
Agenda
Item 4 : EIA Study on the Decommissioning of Cheoy Lee Shipyard
(CLS)
(ACE-EIA Paper 5/2001)
26. The
Chairman welcomed the presentation team led by CE(SD)/CED.
CE(SD)/CED and Associate/MEMC briefed Members
on the paper.
27. The
Chairman asked and Associate/MEMC assured him that
the removal of asbestos-containing material (ACM) would not
create adverse impact on external environment because the
works area was separated from the rest of the shipyard. On
the other hand, only properly registered contractors could
carry out ACM removal work and they would carry out mitigation
measures and monitoring programme to ensure that the works
area was contained. Associate/MEMC also re-affirmed
that no land decontamination work would be initiated at this
stage.
28. In
response to a Member's question, Associate/MEMC said
that the contractor would prevent leakage of asbestos by undertaking
fully contained removal process for high-risk asbestos and
by water spraying for low-risk asbestos.
29. On
a Member's follow up question, Associate/MEMC said
that the contractor would control the amount of water to be
sprayed to avoid draining as ground water. Also, the ground
would be covered with plastic membrane to isolate the asbestos-containing
water and the ground.
30. In
reply to a Member's enquiry, Associate/MEMC said that
the removed ACM would be packed in high-strength, double-layer
bags to be disposed in landfill in accordance with approved
existing practice.
31. The
Chairman concluded that the Subcommittee had no objection
to the ACM removal project and would recommend the proposal
to ACE for endorsement.
Agenda
Item 5 : Status Report on Sand Dredging at West Po Toi Marine
Borrow Area
(ACE-EIA Paper 6/2001)
32. The
Chairman welcomed the presentation team led by CGE(FM)/CED.
CGE(FM)/CED briefly described the content of the paper.
33. The
Chairman drew Members' attention to the fact that West
Po Toi (WPT) was gazetted as a Marine Borrow Area (MBA) in
early 1990s, thus it was exempted from carrying out an EIA
study and from obtaining an environmental permit under the
EIA Ordinance. CGE(FM)/CED said that though it was
exempted under the EIA Ordinance, a comprehensive water modeling
study has been undertaken and had been implemented a vigorous
environmental monitoring and audit (EM&A) programme before
the recent dredging activities.
34. A
Member asked whether the Mainland still supplied sea sand
for the Penny's Bay reclamation project or whether WPT was
the main source. In response, CGE(FM)/CED said that
WPT could not provide sufficient sand for the Penny's Bay
reclamation project. The Mainland would supply about half
of the sand required. CE(SD)/CED added that according
to the plan, the proponent would start obtaining sea sand
from the Mainland in August this year.
35. In
response to a Member's question, CE(SD)/CED clarified
that they had applied for variation of the environmental permit
for Penny's Bay Reclamation so as to modify the combinations
of plant and add in more precautionary measures at the filling
area at Penny's Bay in order to achieve the original dredging
rate. On that Member's follow up question, AD(EA)/EPD
supplemented that the environmental permit for the Penny's
Bay Reclamation controlled the total sediment loading at Penny's
Bay which was at present 25.3kg/second.
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