3       ENVIRONMENTAL LEGISLATION, POLICIES, PLANS, STANDARDS AND CRITERIA

 

3.1             Introduction

3.1.1        Environmental guidelines, policies and management schemes are established to provide guidance on the management of the environment in Hong Kong. The relevant ordinances, Hong Kong Planning Standards and Guidelines (HKPSG) and Practice Notes prepared by the Professional Persons Environmental Consultative Committee (ProPECC) provides a forum for the exchange of views on all environmental matters related to the duties and practice of architects, engineers, planners, surveyors and developers.

 

3.2             Environmental Assessment and Management Scheme

3.2.1        Environmental Impact Assessment Ordinance, Cap. 499

The Environmental Impact Assessment Ordinance (EIAO) (Cap. 499) was enacted on 4th February 1997. The “Technical Memorandum on Environmental Impact Assessment Process” (TMEIA) and two subsidiary laws on the appeal board and application fees were approved by the Provisional Legislative Council in June and November 1997 respectively. The EIAO was implemented on 1st April 1998.

The purpose of the EIAO is to avoid, minimise and control the adverse impact on the environment of designated projects, through the application of the environmental impact assessment (EIA) process and the environmental permit (EP) system. The subject development project is regarded as a designated project with respect to Schedule 2 under the EIAO.

3.2.2        Green Manager Scheme

The Green Manager Scheme[1] (GMS) was set up in January 1994. Under the scheme all government bureaus and departments have to appoint Green Mangers to oversee green housekeeping measures in their offices such as waste minimisation and recovery and energy conservation. They are also asked to make progress reports to the Environment and Food Bureau, which administers and assesses the effectiveness of the Scheme. The GMS will also apply to the subject development, which comprises of the management of several governmental departments.

3.2.3        ISO 14001

The Architectural Services Department was the first Government Department certified to ISO 14001 Environmental Management Systems. The internal and external auditing of the Department covers all aspects of work including the monitoring of all site activities during construction and the designs to minimise environmental impacts of projects.

 

3.3             Air Quality

3.3.1    Air Pollution Control Ordinance, Cap. 311

Air quality legislation is enacted under the Air Pollution Control Ordinance (APCO) (Cap 311) which encompasses all emissions from chimneys, furnaces, ovens or industrial plants.  Under this legislation, Government has declared Air Control Zones (ACZ) for the whole territory.  Air Quality Objectives (AQO) for Hong Kong are given in Table 3.1.

Table 3.1         Hong Kong Air Quality Objectives

Pollutant

Concentration in micrograms per cubic metre (i)

Health Effects of Pollutant at elevated ambient levels

 

Averaging Time

 

 

1 Hourii

8 Hoursiii

24 Hoursiii

 

3 Months iv

 

1 Yeariv

 

Sulphur Dioxide

800

 

350

 

80

Respiratory illness; reduced lung function, morbidity and mortality rates increase at higher levels.

Total Suspended Particulate (TSP)

 

 

260

 

80

Respirable fraction has effects on health.

Respirablev Suspended Particulate (RSP)

 

 

180

 

55

Respiratory illness reduced lung function, cancer risk for certain particles, morbidity and mortality rates increases at higher levels.

Nitrogen Dioxide

300

 

150

 

80

Respiratory irritation; increased susceptibility to respiratory infection, lung development impairment.

Carbon Monoxide

30,000

10,000

 

 

 

Impairment of coordination; deleterious to pregnant women and those with heart and circulatory conditions.

Photo-chemical Oxidants (as Ozone)vi

240

 

 

 

 

Eye irritation; cough; reduced athletic performance; possible chromosome damage.

Lead

 

 

 

1.5

 

Affects cell and body process; likely neuropsychological effects, particularly in children; likely effects on rates of incidence of heart attacks, strokes and hypertension.

Notes:    

(i)            Measured at 298oK (25oC) and 101.325kPa (one atmosphere).

(ii)           Not to be exceeded more than three times per year.

(iii)          Not to be exceeded more than once per year.

(iv)          Arithmetic means.

(v)           Respirable suspended particulars means suspended particles in air with a nominal aerodynamic diameter of 10 micrometres and smaller.

(vi)                Photochemical oxidants are determined by measure of ozone only.

 

3.3.2        Air Pollution Control (Construction Dust) Regulation

The Air Pollution Control (Construction Dust) Regulation stipulated Dust Control Requirements to control the construction dust generated by the construction activities. Dust Control Requirements should be followed throughout the construction period. The contractor should ensure that adequate dust suppression plans have been implemented and fulfill the requirements under the Regulation.

3.3.3    Air Pollution Control (Open Burning) Regulation

Open burning of discarded construction materials and garbage is common at construction sites. In accordance with the Air Pollution Control (Open Burning) Regulation, it is an offence to carry out open burning for the purpose of construction waste disposal and site clearance. Conviction of open burning will be penalised and imprisonment may be resulted for subsequent conviction.

3.3.4    Environmental Impact Assessment Ordinance, Cap. 499

As stipulated in Annex 4 of the EIAO-TMTMEIA, the criterion for odour prediction assessment is to meet 5 odour units based on an averaging time of 5 seconds.

3.3.5        Practice Note for Professional Persons, PN 2/96

ProPECC PN 2/96 – Control of Air Pollution in Car Parks provides air quality guidelines required for the protection of public health and factors that should be considered in the design and operation of car parks in order to achieve the required air quality. This Practice Note provides guidance on the concentration limits on air pollutants: carbon monoxide (CO) and nitrogen dioxide (NO2).

 

3.4       Noise Control

3.4.1    Environmental Impact Assessment Ordinances, Cap. 499 S. 16

The Technical Memorandum (TM) published under Section 16(5) of the Environmental Impact Assessment Ordinance (EIAO) gazetted in 1997, is the fundamental legislation of noise criteria for evaluating noise impact of designated projects.  The Summary of Noise Criteria is given in Table 3.2, Noise Standards for Planning Purposes and, Table 3.3, Noise Standards for Daytime Construction Activities.  The relevant tables are extracted here for ease of reference.

 

Table 3.2         Noise Standards for Planning Purposes

Noise
Sources

 

Noise
Standards


Common Uses

Aircraft Noise
(Noise Exposure
Forecast:NEF)

Helicopter
Noise
Lmax
dB(A)

0700 to
1900 hours

Road Traffic
Noise

Peak Hour
Traffic
L10 (1hour)
dB(A)

Rail
Noise

Fixed Noise
Sources

Kai Tak
Airport

New Chek
Lap Kok
Airport

All domestic premises including temporary housing accommodation

30

25

85

70

(a)
(See Note 3)
The appropriate Acceptable Noise Levels shown in Table 3 of the Technical Memorandum for the Assessment of Noise from Places Other than Domestic Premises, Public Places or Construction Sites and

(b) Lmax (2300 - 0700 hours) = 85dB(A)

(a)
5 dB(A) below the appropriate Acceptable Noise Levels (ANL) shown in Table 3 of the Technical Memorandum for the Assessment of Noise from Places Other than Domestic Premises, Public Places or Construction Sites, or

(b) the prevailing background noise levels (For quiet areas with level 5 dB(A) below the ANL)

Hotel and hostels

30

25

85

70

Offices

30

30

90

70

Educational institutions including kindergartens, nurseries and all others where unaided voice communication is required

30

25

85

65

Places of public Worship and courts of law

30

25

85

65

Hospitals, clinics, convalescence and homes for the aged, diagnostic rooms, wards

30

25

85

55

Notes:    

(i)            The above standards apply to uses which rely on opened windows for ventilation

(ii)                 The above standards should be viewed as the maximum permissible noise levels assessed at 1 m from the external façade

(iii)                Rail noise is under the control of the Noise Control Ordinance and shall comply with the Acceptable

(iv)                Noise Levels laid down in the Technical Memorandum for the Assessment of Noise from Places other than Domestic Premises, Public Places or Construction Sites

 

Table 3.3         Noise Standards for Daytime Construction Activities

Noise Sources

 

Noise
Standards


Uses

0700 to 1900
hours on any
day not being a
Sunday or
general holiday


Leq (30 mins)
dB(A)

1900 to 0700
hours or any
time on
Sundays or
general holiday

·         All domestic premises including temporary housing accommodation

75

(See Note 3)

·         Hotels and hostels

75

·         Educational institutions including kindergartens, nurseries and all others where unaided voice communication is required

70

65
(During examinations)

Notes:     

(i)            The above standards apply to uses which rely on opened windows for ventilation.

(ii)           The above standards shall be viewed as the maximum permissible noise levels assessed at 1m from the external facade.

(iii)          The criteria laid down in the relevant technical memoranda under the Noise Control Ordinance for designated areas and construction works other than percussive piling may be used for planning purpose. A Construction Noise Permit (CNP) shall be required for the carrying out of the construction work during the period.

 

3.4.2    Noise Control Ordinance, Cap. 400

The Noise Control Ordinance (NCO) gazetted in 1988, is the fundamental legislation controlling noise levels in industrial and commercial premises, as well as for construction works. The NCO is enacted through the Technical Memoranda (TM) and Regulations.  The TM relevant to this assessment study is the Technical Memorandum for the Assessment of Noise from Places other than Domestic Premises, Public Places or Construction Sites (TMNP). TMNP details the procedures that should be adopted by the Authority for the measurement and assessment of noise emanating from places other than domestic premises, public places or construction sites. The Acceptable Noise Levels (ANLs) depend on the ASR of the assessment area. Table 3.4 illustrates the ASRs of different types of area containing the NSR. The ANLs are shown in Table 3.5.

Table 3.4         Area Sensitivity Ratings (ASRs)

Type of area containing the NSR

Not

Affected 1

Indirectly Affected 2

Directly Affected 3

(i) Rural area, including country parks or village type developments

A

B

B

(ii) Low density residential area consisting of low-rise or isolated high-rise developments

A

B

C

(iii) Urban area

B

C

C

(iv) Area other than those above

B

B

C

1  Not Affected - NSR is located such that the noise generated by the influencing factors (IF) 4 is not noticeable.

2  Indirectly Affected - NSR is located such that the noise generated by the influencing factors while noticeable, is not a dominant feature of the noise environment.

3  Directly Affected - NSR is located such that the noise generated by the IF is readily noticeable and is a dominant feature of the noise environment.

4  IFs are defined as industrial areas, major roads, or the area within the boundary of Hong Kong International Airport.

 

Table 3.5         Acceptable Noise Levels (ANLs)

 

Area Sensitivity Rating

Time Period

A

B

C

Day (0700 to 1900 hours)

60

65

70

Evening (1900 to 2300 hours)

Night (2300 to 0700 hours)

50

55

60

 

3.4.3        There are no statutory guidelines established on the noise standard for marine traffic noise.  In general, where the intruding noise is significantly higher than the background noise, it may cause nuisance to residents and complaints may be expected.

 

3.5       Waste Disposal

3.5.1    Waste Disposal Ordinance, Cap. 354

The Waste Disposal Ordinance prohibits the unauthorized disposal of wastes, with waste defined as any substance or article which has been abandoned. Construction waste is not directly defined in the Ordinance but is considered to fall within the category of “trade waste”. Trade waste is defined as waste from any trade, manufacturer or business, or any waste building or civil engineering materials, but does not include animal wastes.

Under the Ordinance, wastes can only be disposed of at a licensed site. A breach of these regulations can lead to the imposition of a fine and/or a prison sentence. The Ordinance also provides for the issuing of licenses for the collection and transport of wastes. Licenses are not, however, currently required for the collection of and transport of general construction and/or trade wastes.

3.5.2    Public Cleansing and the Prevention of Nuisances Ordinance, Cap. 132

This regulation provides a further control on littering and illegal dumping of waste on or in public place. The offender shall be liable to a fine of up to HK$25,000 and to imprisonment for 6 months.

3.5.3    Waste Disposal (Chemical Waste) (General) Regulation

Chemical wastes as defined under the Waste Disposal (Chemical Waste) (General) Regulation include any substance being scrap material, or unwanted substances specified under Schedule 1 of the Regulation if such substances occur in a form, quantity, or concentration so as to cause pollution, or constitute a danger to health or risk of pollution to the environment.

Producers of chemical wastes must comply with the Code of Practice on the packaging, labelling, and storage of chemical wastes covered under the Waste Disposal Ordinance. Under this ordinance, a person should not produce, or cause to be produced, chemical wastes unless he is registered with the Environmental Protection Department (EPD).

Producers of chemical wastes must treat their wastes utilising an on-site plant licensed by EPD, or have a licensed collector take the wastes to a licensed facility. For each waste consignment, the waste generator, collector, and disposer must sign all relevant parts of a computerised trip ticket. This will allow the transfer of wastes from cradle to grave to be traced.

The Regulation also describes the storage facilities to be provided on-site, including required labelling and warning signs. To minimise the risks of pollution, and danger to human health, the waste generator is required to prepare and make available written procedures to be observed in the case of an emergency. This “emergency plan” should cover emergencies due to spillage, leakage, fire/explosion, or accidents arising from the storage of chemical wastes. He must also provide emergency response training to those employees who will be handling the wastes or working in the vicinity of the storage area.

3.5.4        Work BureauWorks Bureau Technical Circular No. 4/98 – Use of Public Fill in Reclamation and Earth Filling Projects

This Circular promulgates policy requiring reclamation or earth filling projects with imported fill requirements of 300,000 m3 (three hundred thousand cubic metres) or more to consider using public fill (alternatively termed inert construction and demolition (C&D) material) for the Works.  It amplifies and should be read in conjunction with WBTC No. 2/93 : Public Dumps.  The terminology in current use for what used to be called public dumping but which is now called public filling is shown in the addendum to this circular.

 

3.5.5        Work BureauWorks Bureau Technical Circular No. 4/98A – Use of Public Fill in Reclamation and Earth Filling Projects

This Circular supplements the policy that imported fill requirements of 300,000m3 or more for reclamation or earth filling projects as stipulated in WBTC No. 4/98 which require the project proponent to consider using public fill for the Works are to include also fill demand for surcharge mounds and utility zones.  This Circular also makes some minor amendments to WBTC No. 4/98.

 

3.5.6        Work BureauWorks Bureau Technical Circular No. 5/98 – On Site Sorting of Construction Waste on Demolition Sites

Landfills are being filled up far more rapidly than was programmed and apart from municipal waste the source of much public fill is from construction and demolition sites.  On-site sorting of surplus construction and demolition (C&D) material is therefore desirable so that inert material can be disposed of at public filling areas as far as practicable, and the remaining C&D waste disposed of at landfills.   Dumping Licences for public filling areas require that material to be disposed of at public filling areas must comprise only earth, building debris, broken rock and concrete.  Such materials shall be free from marine mud, household refuse, plastic, metal, industrial and chemical waste, animal and vegetable matter and other matter considered unsuitable by the Filling Supervisor.  Small quantities of timber mixed with otherwise suitable material may be permitted.  The materials considered unsuitable for disposal at public filling areas have to go to a landfill. The terminology ---- in current use has been updated and is shown in the addendum to this circular.

 

3.5.7        Work BureauWorks Bureau Technical Circular No. 5/99 – Trip-ticket System for Disposal of Construction and Demolition Materials

This Circular promulgates the policy to implement a trip-ticket system in PWP contracts for the proper disposal of construction and demolition (C&D) material at public filling facilities or landfills.  Maintenance term contracts are not covered by this Circular.

 

3.5.8        Work BureauWorks Bureau Technical Circular No. 5/99A – Trip-ticket System for Disposal of Construction and Demolition Materials

This Circular amends Works Bureau Technical Circular No. 5/99.

 

3.5.9        Work BureauWorks Bureau Technical Circular No. 19/99 - Metallic Site Hoardings and Signboards

This Circular establishes a new policy requiring the use of metallic site hoardings and signboards in order to reduce the amount of timber used on construction sites.

 

3.5.10    Work BureauWorks Bureau Technical Circular No. 25/99 – Incorporation of Information on Construction and Demolition Materials Management in Public Works Subcommittee Papers

This Circular promulgates the policy and guidelines for incorporating information on the management of construction and demolition material (C&DM) in Public Works Subcommittee (PWSC) papers recommending the upgrading of projects to Category A of the Public Works Programme (PWP) for the implementation of construction works.

 

3.5.11    Work BureauWorks Bureau Technical Circular No. 25/99A – Incorporation of Information on Construction and Demolition Materials Management in Public Works Subcommittee Papers

This Circular amends WBTC No. 25/99 and promulgates the procedures for vetting information on the management of construction and demolition material (C&DM) in Public Works Subcommittee (PWSC) papers, following the policy set out in WBTC No. 25/99.

 

3.5.12    Work BureauWorks Bureau Technical Circular No. 25/99C – Incorporation of Information on Construction and Demolition Materials Management in Public Works Subcommittee Papers

This Circular supplements WBTC No. 25/99 and 25/99A and specifies additional information on construction and demolition material (C&DM) that must be included in Public Works Subcommittee (PWSC) papers. 

 

3.5.13    Work BureauWorks Bureau Technical Circular No. 12/2000 – Fill Management

This Circular sets out the terms of reference and membership composition of the Marine Fill Committee and Public Fill Committee that shall take up the functions and responsibilities of the Fill Management Committee established in June 1989.  It also explains how fill resources, construction and demolition material (C&DM), and dredged/excavated sediment disposal are managed.

 

3.5.14    Work BureauWorks Bureau Technical Circular No. 29/2000 – Waste Management Plan

This Circular introduces the requirement for contractors to prepare and implement a waste management plan (WMP).  The requirement shall be included in all PWP contracts (including design and build contracts but excluding term contracts and contracts administered by Electrical and Mechanical Services Department).  The requirement shall be introduced by way of Particular Specification (PS).  Guidelines for the preparation of the PS clauses are provided in this Circular.

 

3.6             Water Quality

3.6.1    Water Pollution Control Ordinance, Cap. 358

Water quality in Hong Kong is legislated by the provisions of the Water Pollution Control Ordinance (Cap 358), 1980 (WPCO). Through an amendment to the original legislation, Territorial Water has been subdivided into ten Water Control Zones (WCZ) with each WCZ being ascribed a series of Beneficial Uses (BU) and related statutory Water Quality Objectives (WQO) reflecting the assimilative capacity of the water body, or parts thereof, and its predominant uses. The study area lies within North Western Water Control Zone which was declared in 1992.

In 1991, a Technical Memorandum on Standards for Effluents discharged into Drainage and Sewerage Systems, Inland and Coastal Waters, referred to as the Technical Memorandum on Effluent Standards (TMES) was issued. This Technical Memorandum requires the licensing of all discharges, and sets comprehensive standards for discharges into all public sewers and drains, as well as all receiving waters, both inland and coastal.

3.6.2    Practice Note for Professional Persons, ProPECC PN 5/93

As presented in ProPECC PN 5/93, Building (Standards of Sanitary Fitments, Plumbing, Drainage Works and Latrines) Regulations 40(1), 40(2), 41(1) and 90, foul water should be discharged to a foul water sewer and surface water should be discharged via rainwater pipes to stormwater drains. The water quality standards will have to be met during all construction stages.

3.6.3    Practice Note for Professional Persons, ProPECC PN 1/94

This Practice Note provides some basic environmental guidelines for the handling and disposal of construction site discharges. Eight types of discharges from construction sites have been identified:

(i)            Surface runoff;

(ii)          Groundwater;

(iii)         Boring and Drilling Water;

(iv)        Wastewater from Concrete Batching & Precast Concrete Casting;

(v)          Wheel Washing Water;

(vi)        Water for Testing & Sterilisation of Water Retaining Structures and Water Pipes;

(vii)       Water from Building Construction;

(viii)      Acid Cleaning, Etching and Pickling Wastewater

 

3.7       Hazard to Life

3.7.1    Practice Note for Professional Persons, ProPECC PN 2/94

General information and requirements on the Potentially Hazardous Installations (PHI) are provided in this Practice Note. There are existing 34 PHIs in Hong Kong. They include the larger LPG storage facilities, gas works, chlorine stores at water treatment works and explosives factories and depots. Relevant Government contacts are also listed in this Practice Note for further information.

3.7.2        Hong Kong Planning Standards and Guidelines (HKPSG), Chapter 11

Chapter 11 of HKPSG provides planning standards and guidelines on the land uses or facilities related to the installation or located within the consultation zone of PHI. According to the definition of PHI in this Chapter, a PHI is an installation which stores hazardous materials in quantities equal to or greater than a specified threshold quantity, which varies with different substances. The risk guidelines and requirements for the undertaking of hazard assessment (HA), planning studies (PS) and action plans (AP) for existing and proposed PHI are introduced in this Chapter.

3.7.3    Environmental Impact Assessment Ordinance, Cap. 499

Annex 4: Criteria for Evaluating Air quality Impact and Hazard to Life of TMEIA listed criterion for hazard to human life according to the Risk Guidelines as shown in Figure 1 of Annex 4.



[1] Environment 2000, Environmental Protection Department, Hong Kong. 1999