6.                     Solid WASTE MANAGEMENT

 

6.1                   Introduction

 

6.1.1             This section identifies the type of wastes that are likely to be generated during the construction of the proposed Roads D1, D8 and D10 and extended Road P2 and assesses the potential environmental impacts that are associated with the handling and disposal of these wastes. Mitigation measures and good site practice, including waste handling, storage and disposal, are recommended with reference to the applicable legislation and guidelines.

 

6.1.2             The operation of the proposed Roads D1, D8 and D10 and extended Road P2 will generate wastes associated with littering and road maintenance activities, and the amount is expected to be minimal.  The potential environmental impacts arising from the handling and disposal of this small amount of wastes is anticipated to be negligible and therefore have not been evaluated further in this report.

 

6.1.3             The construction of Roads D1, D8 and D10 and extended Road P2 will mainly involve earthworks excavation and road pavement, except in the case of Road D10 where the foundation of the section across the Eastern Drainage Channel will require bored piling. The main issues having waste management implications during construction are (i) workforce wastes, (ii) chemical wastes, and (iii) construction and demolition (C&D) material.

 

6.2                   Environmental Legislation, Policies plans and Standards

 

Waste Management

 

6.2.1             The principal legislation for waste collection and disposal is the Waste Disposal Ordinance (Cap 354) which provides a licensing system for the collection and disposal of waste.  Enacted in 1980, this ordinance generally encompasses all stages of the waste management chain, from place of arising to final disposal point.  Under the Waste Disposal Ordinance (WDO), construction waste is classified as trade waste and the Contractor is thus responsible for their disposal.  Chemical waste is controlled under the Waste Disposal (Chemical Waste) (General) Regulation under the Waste Disposal Ordinance. This regulation controls the possession, storage, collection, transport and disposal of chemical waste.

 

6.2.2             The Public Health and Municipal Services Ordinance (Cap 132) contains controls for the prevention of nuisance from solid waste.

 

6.2.3             The Hong Kong Planning Standards and Guidelines (HKPSG), Chapter 9 (Environment), provides additional information on regulatory compliance, and on the required methods of treatment and disposal of different types of waste. 

 

6.2.4             Annex 15 of Technical Memorandum on the EIA Process (EIAO-TM) sets out guidelines for assessment of waste management implications.

 

Construction and Demolition (C&D) Material

 

6.2.5             The current policy relating to the disposal of construction and demolition (C&D) material is documented in the Works Bureau Technical Circular No. 2/93B, ‘Public Filling Facilities’.  In order to dispose of the inert portion of C&D material in a public filling facility, a licence is required which is issued by the Civil Engineering Department (CED).  The Works Branch Circular states that C&D material suitable for use as fill material should not be disposed of to landfill, but placed in a public filling facility for reclamation and land formation projects.  The Public Fill Committee (PFC) together with Project Departments are responsible for considering the suitability of a site as a public filling facility.

 

6.2.6             In addition to the Works Bureau Technical Circular, EPD and CED have produced a leaflet titled `New Disposal Arrangements for Construction Waste' which states that only construction waste with less than 30% by weight of inert material will be accepted at landfill.  If the material contains more than 30% inert material, the waste must be sorted with suitable material sent to a public filling facility.

 

6.2.7             The following circulars also relate to C&D material management :

 

§           WBTC No. 1/96, Wet Soil in Public Dumps;

§           WBTC Nos. 5/99 & 5/99A, Trip-ticket System for Disposal of Construction and Demolition Material;

§           WBTC No. 18/99, Particular Specification Clause for Vehicles Carrying Dusty Materials:

§           WBTC No. 19/99, Metallic Site Hoardings and Signboards;

§           WBTC Nos. 25/99, 25/99A & 25/99B, Incorporation of Information on Construction and Demolition Material Management in Public Works Subcommittee Papers;

§           WBTC No. 12/2000, Fill Management; and

§           WBTC No. 29/2000, Waste Management Plan.

 

Chemical Waste

 

6.2.8             The Waste Disposal (Chemical Waste) (General) Regulation controls the storage, collection, transportation and disposal of chemical wastes in Hong Kong.  Under the Regulation, a chemical waste includes any substance which is a scrap material or by-product arising from industrial/trade activities, as specified under Schedule 1 of the Waste Disposal Ordinance (WDO), in such form, quantity and concentration that it will cause pollution or constitute a danger to health or risk to the environment. A complete list of such substances is provided under the Ordinance. A chemical waste producer will be required under the Ordinance to register with the Director of Environmental Protection and to dispose of chemical waste to a licensed treatment facility such as the Chemical Waste Treatment Centre (CWTC) located at Tsing Yi, which was commissioned in June 1993 and is designed to treat most of the chemical waste from the territory.  In addition, any contractor employed for the collection of chemical waste must be a registered chemical waste collector under the Ordinance.

 

 

 

6.3                   Assessment Methodology and Criteria

 

6.3.1             The criteria for evaluating the potential construction waste management implications are set out in Annex 7 of the EIAO-TM.  The methods for assessing potential waste management impacts during construction follow those presented in Annex 15 of the EIAO-TM and include the following:

 

§           estimation of the types and quantities of the wastes generated;

§           assessment of potential impacts from the management of solid waste with respect to potential hazards, air and odour emissions, noise, wastewater discharges and transport; and

§           impacts on the capacity of waste collection, transfer and disposal facilities.

 

6.4                   Environmental Impact Identification, Prediction and Evaluation 

 

WORKFORCE WASTES

 

6.4.1             Marine pollution from general refuse (food scraps, paper, empty containers etc) should not be permitted because of the detrimental effects on water quality in the area.  Rapid and effective collection of site waste will be required to prevent waste materials being blown around by wind, flushed or leached into the marine environment.  Putrescible waste will not be suitable for incorporation into any reclamation works.

 

6.4.2             The amount of general refuse will be largely dependent on the size of the workforce employed by the contractor and cannot be quantified at this time as no information on the number of workers is available at this stage.  The amount of general refuse expected to be generated will be quantified in the site Waste Management Plan to be prepared by the Contractor.  With the implementation of waste management practices at the site, adverse environmental impacts are not expected to arise during the construction works. 

 

Chemical Wastes

 

6.4.3             Construction plant and equipment will require regular maintenance and servicing which will generate chemical waste such as cleaning fluids, solvents, lubrication oil and fuel.  Vehicle maintenance will also involve the use of a variety of chemicals and lubricants, including heavy duty cleaners, organic solvents, degreasers, brake fluids, battery acid and soldering fluids.

 

6.4.4             Chemical wastes arising during the construction phase may pose serious environmental, health and safety hazards if not stored and disposed of in an appropriate manner as outlined in the Chemical Waste Regulations.  These hazards include:

 

·          toxic effects to workers;

·          adverse impacts on water quality from spills and adverse impacts on marine biota; and

·          fire hazards.

 

6.4.5             Materials classified as chemical wastes will need special handling and storage arrangements before removal for appropriate treatment at the chemical waste treatment facility (CWTF) at Tsing Yi.  Wherever possible opportunities should be taken to reuse and recycle materials.

 

6.4.6             It is difficult to quantify the amount of chemical waste which will arise from the construction activities since it will be highly dependent on the Contractor’s on-site maintenance requirements and the number of plant utilised.  However, it is anticipated that the quantity of chemical waste, such as lubricating oil and solvent produced from plant maintenance, will be small and in the order of a few hundred litres per month. The amount of chemical waste expected to be generated will be quantified in the site Waste Management Plan to be prepared by the Contractor.

 

Construction and Demolition (C&D) Material

 

6.4.7             Construction and demolition material will include surplus construction material or unwanted materials generated during construction activities and may comprise:

 

§           wood from formwork and falsework;

§           materials packaging and equipment wrappings;

§           unusable / surplus concrete / grouting mixes; and

§           damaged or contaminated surplus construction materials.

 

6.4.8             If not managed properly, the storage, handling, transport and disposal of C&D material have the potential to create visual, water, dust and traffic impacts. C&D material should be sorted on-site into inert materials (public fill) which should be re-used on-site as far as possible or disposed of to public filling facility, and C&D waste which may need to be disposed of to landfill. Marine pollution from this waste should not be permitted because of the potential to cause water pollution and indirect impacts on marine biota.  Mitigation measures should include provision of a collection area where waste can be stored and loaded prior to removal from the site.  The volume of surplus construction material generated will be dependent on the Contractor’s operating procedure and practices and cannot be quantified at this early stage as no detailed construction programme is currently available for the Project.  However, with respect to the nature of construction activities, it is anticipated that the quantity will be small.

 

6.4.9             Given that the construction works for the proposed roads are on existing and new reclamation, there will be minimal generation of C&D waste as no existing facilities or structures would require demolition.  The major type of C&D material generated will be excavated material from the foundation construction works for Roads D1 and D10, as discussed below.

 

6.4.10         It is estimated that approximately 10,000 m3 of excavated material will be generated from the foundation construction of Roads D1 and D10, and a total of 50,000 m3 of fill materials will be required for the construction of road embankments of the three Roads D1, D8 and D10 (see Table 6.1). Based on the preliminary estimate that about 10% of the excavated material will be unsuitable to be reused on-site, the quantity of excavated materials to be disposed off-site will be small (about 1,000 m3).  A detailed construction programme is currently not available for the roads, and therefore the timing for the generation of excavated material will be given in the site Waste Management Plan.  The tentative timing of foundation works for Road D10 is indicated in Figure 2.4

 

6.4.11         Excavated material from Road D10 requiring off-site disposal would comprise marine mud and alluvium.  The excavated material from Road D1 requiring off-site disposal would comprise reclamation fill (i.e. public fill) and would be suitable for disposal to a public filling facility. It is considered that the additional traffic arising from transporting this amount of excavated materials will not be adverse. In order to reduce the impacts from off-site transportation of excavated materials, the reclamation fill material should be reused on-site as fill materials for site formation and construction of road embankment as far as possible.

 

Table 6.1      Estimated Earthworks Quantities for the Construction of Roads D1, D8 & D10

 

Road Description

Excavation

Volume (m3)

Fill volume

(m3)

Disposal volume

(m3 )

Road D1 including D1/D10 roundabout

7,500

32,000

750 (public fill)

Road D8

-

8,000

-

Road  D10

2,500

10,000

250 (C&D waste)

Extended Road  P2

 

85,000

 

Total

10,000

 

1,000

 

6.4.12         The agreed alignment of Road D10 falls inside the boundary of the TKO Stage 1 landfill at Area 77, although the proposed pile locations will not encroach on the waste boundary at Area 77.  An issue specific for the section of Road D10 adjacent to Area 77 is the possibility that the excavated material may be contaminated by leachate seepage from the TKO Stage 1 landfill.  It is therefore recommended that the excavated material from the foundation construction (approximately 250m3) be considered as contaminated material and disposed off-site to existing operating landfill.  It is anticipated that the excavated material from the Road D10 construction works not adjacent to Area 77 will be suitable for reuse on-site.

 

6.4.13         EPD have advised that marine mud excavated from bored piling construction for Road D10 should be disposed of by marine dumping in order to conserve limited and valuable landfill void space.  For marine disposal of the excavated mud, the requirements of WBTC No. 3/2000 ‘Management of Dredged/Excavated Sediment’ should be followed. Site investigation works would be carried out at the detailed design stage in the area of proposed pile foundations to determine the material type.  In the unlikely event that refuse is found in the area of piling, possible disposal methods of the mixed refuse/marine mud material would be examined.  As EPD have advised that refuse is generally not allowed to be disposed of at marine dumping ground, the mixed material is likely to require dewatering prior to disposal to landfill.

 

 

6.5                   Mitigation of Adverse Impacts

 

GOOD Site PRACTICE

 

6.5.1             It is anticipated that adverse waste management related impacts would not arise, provided that good site practices are adhered to.  Recommendations for good site practices for the construction waste arising include:

 

·          Nomination of an approved person, such as a site manager, to be responsible for the implementation of good site practices, arranging for collection and effective disposal to an appropriate facility, of all wastes generated at the site

 

·          Training of site personnel in proper waste management and chemical handling procedures

 

·          The reuse and recycling of materials wherever possible

 

·          Plan and stock construction materials carefully to minimise amount of waste generated and avoid unnecessary generation of waste

 

·          Provision of sufficient waste disposal points and regular collection for disposal

 

·          Provision of an enclosed collection point for storage and containment

 

·          Separation of chemical wastes for special handling and appropriate treatment at the Chemical Waste Treatment Facility

 

·          Regular cleaning and maintenance programme for drainage systems, sumps and oil interceptors.

 

·          Develop procedures such as a ticketing system to facilitate tracking of loads and to ensure that illegal disposal of waste does not occur.

 

·          Maintain records of the quantities of wastes generated, recycled and disposed.

 

6.5.2             In addition to the above good site practices, specific mitigation measures are recommended below for the identified construction waste arisings:

 

General Site Wastes

 

6.5.3             A collection area shall be provided where waste can be stored prior to removal from site.  An enclosed and covered area is preferred to reduce 'wind blow' of light material.  If an open area is unavoidable for the storage or loading/unloading of wastes, then the area shall be bunded and all the polluted surface run-off collected within this area shall be treated and discharged into drainage system.

 

 

 

Workforce Wastes

 

6.5.4             Suitable collection sites around site offices and canteen will be required.  It is recommended that for environmental hygiene reasons putrescible wastes are not stored for a period exceeding 48 hours, however, removal every 24 hours is preferable.

 

Chemical Wastes

 

6.5.5             The Contractor will be required to register as a chemical waste producer with EPD if chemical waste is produced.  After use, chemical waste (eg. cleaning fluids, solvents, lubrication oil and fuel) shall be handled according to the Code of Practice on the Packaging, Labelling and Storage of Chemical Wastes.  Any unused chemicals or those with remaining functional capacity shall be recycled.  Spent chemicals shall be properly stored on site within suitably designed containers, and shall be collected by an approved operator for disposal at the Chemical Waste Treatment Facility or other licenced facility in accordance with the Waste Disposal (Chemical Waste) (General) Regulation under the Waste Disposal Ordinance.

 

6.5.6             Any service shop and minor maintenance facilities shall be located on hard standings within a bunded area, and sumps and oil interceptors shall be provided.  Maintenance of vehicles and equipment involving activities with potential for leakages and spillage shall only be undertaken with the areas appropriately equipped to control these discharges.

 

Construction and Demolition (C&D) Material

 

6.5.7             Careful design and planning together with good site management can reduce over-ordering and generation of C&D materials such as concrete, mortar and cement grouts. Formwork shall be designed to maximise the use of standard wooden panels, so that high reuse levels can be achieved. Alternatives such as steel formwork or plastic facing shall be considered to increase the potential for reuse.  C&D material will also be generated from excavation activities.  The C&D material shall be separated on-site into three categories: (i) public fill, the inert portion of the C&D material (e.g. concrete and rubble), which shall be re-used on-site or disposed of at a public filling facility; (ii) C&D waste for re-use and/or recycling, the non-inert portion of the C&D material, (e.g. wood, glass, plastic, steel and other metals); (iii) C&D waste which cannot be re-used and/or recycled.  The waste producers are responsible for its disposal at strategic landfills.

 

6.5.8             In order to minimise the impact resulting from collection and transportation of material for off-site disposal, it is recommended that inert material shall be re-used on-site where possible.  Excavated fill material from Roads D1 and D10 foundation works should be reused on-site as fill materials for site formation and construction of road embankment as far as possible.  Prior to disposal of C&D material, it is recommended that wood, glass, plastic, steel and other metals shall be separated for re-use and/or recycling where practicable to minimise the quantity of waste to be disposed of to landfill.

 

6.5.9             When disposing C&D material at a public filling facility, it shall be noted that the material shall only consist of earth, building debris and broken rock and concrete.  The material shall be free from marine mud, household refuse, plastic, metals, industrial and chemical waste, animal and vegetable matter, and other material considered to be unsuitable by the Filling Supervisor.  Small quantities of timber mixed with otherwise suitable material would be permitted.

 

6.5.10         In order to monitor the disposal of C&D waste at landfills and to control fly tipping, a trip-ticket system should be included as one of the contractual requirements and implemented by an Environmental Team undertaking the Environmental Monitoring and Audit work.  An Independent Environmental Checker should be responsible for auditing the results of the system.

 

6.5.11         It is recommended that, where practicable, public fill be used instead of imported general fill for earthfilling related activities for the Project.  The imported public fill should be obtained off-site from other public fill stockpile areas.  The use of suitable recycled C&D materials in the road formation contract should be considered at the detailed design stage if recycling facilities/sources are available.  This would be in accordance with WBTC No. 31/2000, ‘Specification Allowing the Use of Recycled Inert Construction and Demolition Material.’  There is currently a sorting facility at Area 137.  CED have plans to upgrade this facility to a recycling plant however this proposal is very preliminary.

 

C&D material from road d10 foundation construction adjacent to area 77

 

6.5.12         As a precautionary measure trial pits will be dug during the construction of the piers for Road D10 to ensure that there is no waste material at the piling foundation.  It is recommended that the excavated material from the foundation construction be considered as contaminated material and disposed off-site to existing operating landfill.  The existing seawall adjacent to the Road D10 alignment is a rubble mound seawall and will allow some movement of sea water.  The excavated material is likely to be of high moisture content and therefore dewatering may be required before disposal of the material to landfill (so as to meet the permitted waste type requirements on water content).  Marine mud excavated from the bored pile foundation works for Road D10 will require marine disposal in order to conserve landfill void space.

 

6.6                   Definition and Evaluation of Residual Environmental Impacts

 

6.6.1             With the implementation of the recommended mitigation measures for the handling, transportation and disposal of the identified waste arisings, no residual impact is anticipated during the construction of the proposed road developments.  

 

6.7                   Conclusion

 

6.7.1             Wastes generated by the construction activities are likely to include C&D materials, workforce waste and chemical waste.  Provided that these identified waste arisings are handled, transported and disposed of using approved methods and that the recommended good site practices are strictly followed, adverse environmental impacts are not anticipated.  The recommended mitigation measures shall form the basis of the site Waste Management Plan to be developed by the Contractor at the commencement of the construction phase. 


 

6.7.2             Table 6.2 provides a summary of the various waste types likely to be generated during the construction phase, together with the recommended handling and disposal methods.

 

Table 6.2         Summary of Waste Handling Procedures and Disposal Routes

 

Waste Type

 

Handling

Disposal

Construction & Demolition Material

 

 

Where possible should be re-used on-site

 

 

If off-site disposal required, separate into:

·           Public fill (e.g. concrete, rubble, earth)

 

·           C&D waste for re-use and/or recycling (e.g. wood, plastic, steel and other metals)

 

·           C&D waste which cannot be re-used and/or recycled

 

On-site as fill materials for site formation/road embankment

 

Public filling facillity or reclamation

 

To be determined at a later stage

 

 

Landfill

·            Excavated Material from Road D10 foundation construction adjacent to Area 77: Dewatering if necessary to meet permitted water content requirement for disposal to landfill

 

Landfill

·           Excavated Mud from Road D10 foundation works within Eastern Drainage Channel: Non-displacement type bored piling to drive temporary steel casing through the soft mud prior to excavation of the material within the casing

 

Marine disposal

Maintenance and Chemical Wastes

Recycle on-site or by licensed companies

Stored on-site within suitably designed containers

 

By licenced contractor to Chemical Waste Treatment Facility

Workforce Wastes

Provide on-site refuse collection facilities

 

Landfill, collection by

private hygiene company