LC Paper No. PWSC106/16-17(01)

發展局規割地政科

香港添馬添翼道二號

政府總部西翼十t樓

本局檔號 Ollr Ref.

來函檔號 YOllr Ref.

DEVB(PL-P) 50/01 /75

Ms Sharon CHUNG Legislative Council Secretariat Public Works Subcommittee Legislative Council Complex 1 Legislative Council Road Central, Hong Kong

Dear Ms Chung,

(Translation)

Planning and Lands Branch Development Bureau

17沛， West Wing Central Government Offices 2 Tim Mei A venue, Tamar

Hong Kong

電吉舌 Te1.: 3509 8810

傳真 Fax: 2868 4530

Bv Email

13 March 2017

Capital Works Reserve Fund Block Allocation

Enquiry from Hon CHU Hoi圓dick

on Individual Project (Kwu Tung North and Fanling North New Development Areas)

We refer to the letter dated 18 February 2017 addressed to the Chaitman of the Public Works Subcommittee from Hon CHU Hoi-dick seeking inforτnation on individual project under Capital Works Reserve Fund Block Allocation. As requested by the Chairman, we have coordinated information provided by the relevant bureaux/departments and the reply is as follows (in accordance with the order and numbering of the incoming letter) :

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(1) Funding Allocation Arrangement for Land Acquisition Costs in

respect of Kwu Tung North and Fanling North New Development

Areas (KTN and FLN NDAs)

Land acquisition costs incurred by public works are calculated

according to the mechanism approved by the Finance Committee (FC) and

payable under Head 701 of the Capital Works Reserve Fund (CWRF). In

accordance with the financial procedures, funding allocations 企omC兩位F for

block al1ocations, including the said expenditure on land acquisition costs

under Head 701 , shall be approved by FC in examining the Estimates of each

financial year. As the said costs are calculated according to the approved

mechanism and payable under Head 701 according to the established practice,

funding will be provided as mentioned above by following the general

financial procedures without having to seek separate funding approval. As

stated by the Government on the announcement of the North East New

Tenitories New Development Areas project in 2013, land resumption and

compensation costs fo1' KTN and FLN NDAs were estimated to exceed $30

billion in total. However, the scope of the Advance, First Stage and the

remaining works ofthese two NDAs, and the ac仙al area of and expenditure on

land resumption are pending confirmation. No detailed estimation by phases

of the costs is thus available.

(2) First Stage of Site Formation and Engineering Infrastructure at

KTN and FLN NDAs

As the KTN and FLN NDAs project spans a verγlarge area, the project

is expected to take more than ten years from commencement of the [11'st phase

to overall completion. To facilitate project management, we will carry out the

project in phases. The Govelnment will proceed with the development in order

of priority. The First Stage Works (Annex 1) is part of the first phase of the

NDAs development. Its scope comprises the following:

(i) Site formation works in designated areas; (ii) Development of the Long Val1ey Nature Park;

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(iii) Provision of associated engineering infrastructure, including drainage, sewerage, waterwo1'ks, envi1'onmental mitigation measures, etc; and

(iv) Construction supervision.

The detailed design and site investigation for the First Stage Works was included in Category D of the Public Works Programme in June 2014, and commenced in November 2014. The Agreement number is CE 13/2014 (CE) (including Advance Works and First Stage Works) with AECOM Asia Company Limited as the Consultants.

(3) Purpose-built Complex of Residential Care Homes for the Elderly (RCHE) in KTN NDA

(a) Purpose-built RCHE Complex Project

For early completion of the RCHE Complex in Area 29 of KTN NDA, the Govelnment had brought forward its funding application for resumption of PI甘ate land and implementation of the associated site formation and infrastructure works, which was approved via Block Allocations under Capital Works Reserve Fund by the Finance Committee of the Legislative Council at its meeting on 19 March 2016. Fo1' the revised estimate of $360 million for “Land Resumption for Construction of the Purpose-built Complex of Residential Care Homes for the Elderly in Area 29 ofKwu Tung No1'th NDA", the Government anticipates that it will be paid in the 2016-17 finan.cial year.

Acco1'ding to the cunent project prograrnme, if the site formation and associated inf全部tructure works and the building works of the RCHE Complex are progressing smoothly, the Government would strive for completion of the RCHE Complex in 2022 for anticipated operation in 2023.

To cope with the Advance Works of KTN NDA, the existing RCHEs in Dills Corner Garden (DCG) would be cleared in two phases. The first phase is expected to be carried out at the end of 2018 while the second phase would be conducted afte1' the completion of the RCHE Complex. A few blocks in DCG would be affected by the fi1'st phase clearance including those cUlTently used as RCHEs. If necess訂y， we would modi命 the existing

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non次CHE b10cks in DCG to RCHEs for accornmodation of the e1der1y

affected by the first phase clearance such that they do not need to move out

企om' DCG before the operation of the RCHE Comp1ex. Re1evant

departments wou1d closely discuss on how to time1y complete the project and

reduce the impact on the elderly in the RCHEs in DCG. We could only confirm

the timetable for the first phase clearance after approva1 of the Legislative

Counci1 on the funding application for the Advance Works of KTN NDA.

As indicated at the Legis1ative Council Pane1 on We1fare Services on

12 May 2014, in allocating the subsidised residentia1 care p1aces of the new

RCHE comp1ex, priority wou1d be given to e1igib1e existing residents at DCG

who have passed the care needs test under the Standardised Care Need

Assessment Mechanism for Elderly Services (SCNAMES) before its service

commencement. F or those residents who have not passed the care needs test

or not been assessed under SCNAMES by the time of service cornmencement,

the Socia1 We1fare Department will assist them in finding a1ternative

p1acements in other private RCHEs.

(b) Treatment of Arsenic-containing 80il in the 8ite of the RCHE

Complex

The arsenic in the soi1 at KTN NDA is naturally oCCUlTing. We had

already caITied out a HRA to ensure that the land 扭曲e NDA could be used

safe1y in future. According to the results of the ground investigation, the

arsenic concentrations of the soil samp1es collected at the shallow ground

region of the new RCHE Complex (within 4m below the site f01mation 1evel)

ranged 企om 4mg/kg to 1,200mg/kg. For those samp1es collected at deep

g1'ound (outside 4m be10w the site formation leve1), thei1' a1'senic

concentrations ranged from 1mg/kg to 3,680mg/kg. We wou1d carrγout

treatment for the soi1 with arsenic concentration greate1' than 571mg/kg in

accordance with the 1'ecornmendations of the HRA in the Environmenta1

Impact Assessment (EIA) Report.

Appendix 8.1 of the EIA Report fo1' the No1'th East New Territories

們ENT) NDAs mainly covers the treatment of the man-made contaminated

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land while the treatment of the naturally occuning arsenic in soil should fo l1ow Appendix 8.4 of the EIA Report. For the pmpose-built RCHE Complex in Area 29 of KTN NDA, we had already submitted contamination assessment plan to Environmental Protection Department (EPD) in accordance with the requirements of the EIA Report. Based on the assessment results, there is no contaminated land-use / activities found at the RCHE Complex site.

The arsenic-containing soil at the RCHE Complex site is natu1'al1y occuning and is mainly originated from the Ash Crystal Tuff in the region, rather than arising 企om man-made contamination. In undertaking the NENT NDAs EIA, the Govemment had already canied out a HRA for the arsenic-containing soil in KTN to study its characteristics and develop suitable health risk baseline and con'esponding treatment method in order to ensure public safety.

For the HRA fo1' KTN NDA, we had already developed a suitable health risk baseline and co訂esponding treatment method according to the HRA method commonly used international1y. The baseline and treatment method were developed by assessing the proportions of arsenic entering the human body through different exposure pathways and referencing to the hygiene safety index of W or1d Health Organisation (明在10) and United States Environmental Protection Authority (USEP A). Based on the results of the HRA, the identified safety index is that solidification / stabilisation should be canied out for the soi1 with arsenic concentration greater than 571mg/kg in order to ensure public safety.

During consttuction stage, the contractors should use specific method to solidify the arsenic in the soil according to the recommendations ofthe HRA of the EIA Report in order to ensure that such arsenic would not affect the public health after completion of the development. We would implement appropriate mitigation measures based on the recommendations of the HRA of the EIA Repo此， which include provision of relevant training, equipment and materials to the workers. Masks, respiratory apparatus and personal protective equipment would also be provided to the workers where necessary.

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(4) RCHE Complex in Kwu Tung, Ground Investigation Works in KTN

NDA, Decontamination Assessment under KTN NDA and Lok Ma

Chau Loop Development

Pursuant to the relevant requirements of the EIA Ordinance, the EIA

Report for the NENT NDAs, which was approved with conditions in 2013 , had

been deposited at the following website for public viewing

h吐口 ://www.epd.立oV.hk/eia/ register/report/eiareport/eia 2132013/. An

executive summary (Chinese version) of the EIA Repo此 is also available to

highlight the project scope and key findings of the EIA study. Details of the

EIA fmdings can be found in the full EIA Report in English. As the

treatment works for arsenic-containing soil have not yet commenced on site,

no relevant documentation or inspection records are available at this stage.

Based on the recommendations from the HRA in the EIA Report, soil

with arsenic concentration above 571 mg/kg will require treatment by

solidificationlstabilisation (S/S) method to ensure 也at no adverse impacts wi11

be posed to public health after completion of the NDAs development. The

S/S treatment method is a simple and well-established ground remediation

technique with international applications and local experiences. To take

forward the HRA reconunendations, we engaged the Hong Kong Polytechr吐c

University (PolyU) to cany out further study on arsenic-containing soil, and to

help formulate app1'op1'iate treatment plan fo1' KTN NDA. The PolyU study

also confi1'med that S/S treatment is effective and robust fo1' treating the soil

with arsenic level exceeding the 571 mg/kg threshold in KTN NDA. With

the implementation of effective S/S treatment, the treated soil wil1 comply with

the health 1'isk standards as stipulated in the HRA and pose no harrn to human

body. We will require the contracto1's to carry out soil sampling regular1y

during the construction phase and conduct Toxicity Leaching Procedu1'e Test

(TCLP test) to ensure the treated soil will comply with the above health risk

standa1'ds.

The arsenic-containing soil in K甘\f NDA is fundamentally different

from that in Lok Ma Chau (LMC) Loop in telms of or海in and nature. The

arsenic in LMC Loop soil is fOlmed by anthropogenic contamination, whereas

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the arsenic in KTN soil is due to natural geological formation. F or LMC Loop, the area was used in the past as a dumping ground for contaminated sediments extracted from training works at Shenzhen River. Since the contamination is man-made, the environmental assessment and remedial measures will have to follow the 1'elevant local standa1'ds fo1' contaminated land such as the “Guidance Note for Contaminated Land Assessment and Remediation" and “Risk-based Remediation Goals fo1' Contaminated Land Management (RBRG)" promulgated by the Environmental Protection Department (EPD). In contrast, the above contamination standards do not apply in the KTN context due to the geogenic nature of arsenic in KTN soil. To ensure public safety, the Government had conducted an independent HRA during the EIA study to detelmine the acceptable health risk levels for arsenic exposure and devise suitable treatment method for minimising the risks associated with soil with higher arsenic level. The health risk levels adopted in the HRA are formulated with reference to international guideline values accepted by the W orld Health Organization (可在1:0) and the United States Environmental Protection Agency (USEPA). For LMC Loop, the volume of the soil to be treated can be found in the EIA Report for the project. For KTN NDA, the soil treatment volume is detelmined on the basis of the ground investigation data obtained during the EIA study. As a result of the different origin and nature of the arsenic containing soil in LMC Loop and KTN NDA, we formulated appropriate treatment strategies based on the soil properties and the potential risk to the area. There is no question of applying double treatment standard for the sake of cost or other factors.

We are now conducting ground investigation works at accessible locations in KTN NDA to determine the spatial distribution of arsenic-containing soil. Results will be available after completion of all ground investigation works, and will be used to establish the treatment extent. We will incorporate necessary environmental mitigation measures into contract provision to control the impacts arising 企om noise, dust and eff1uent from the works to comply with established standard and guidelines. All 甘eatment

works fo1' arsenic-containing soil will be carried out in accordance with the requirements of the EIA Report to minimise environmental nuisance. As for othe1' developments in K甘.J NDA，臼rther assessment is required to identi方

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the extent of t1'eatment of arsenic containing soil after completion of the

ground investigation. For private developments, the relevant lease conditions

will stipulate that the developer will follow the requirements in the EIA Report

to carry out treatment works of a1'senic containing soil within the deeper soil in

order to safeguard public health and safety.

D1'inking water that is polluted with a1'senic is a majo1' source of

arsenic intake fo1' humans, followed by ingestion of a1'senic-contaminated food.

Relevant departments (including Department of Health, Agriculture, Fisheries

and Conservation Department and Envi1'onmental P1'otection Department) had

assessed that the p1'esence of arsenic in KTN soil would not pose adverse

health impacts to the public in its existing state. No abnormal arsenic content

was found during the routine testing performed by Agriculture, Fishe1'ies and

Conservation Department on samples of water from streams and wells, vegetable p1'oducts and pond fish collected in KTN area. In addition, all

drinking water will be treated befo1'e supplying to households in KTN NDA

through pipe netwo1'k. The1'efo1'e, the 1'isk of a1'senic uptake 企om food 0 1'

wate1' sources is minimal in K甘..J NDA. Based on the PolyU study, most of

the a1'senic in KTN NDA exists in the fo1'm of ferric arsenate, which exhibits

low solubility, high stability, and is unlikely to contaminate the groundwater in

the region.

As 1'egards solid waste, we are committed to avoiding and minimising

construction and demolition (C&D) materials t趾ough planning, design and

construction management to achieve sustainable development. Acco1'ding to

our preliminary estimate, all excavated materials in KτN and FLN NDAs, including the t1'eated arsenic-containing soil, would be 1'eused as filling

materials fo1' construction wo1'ks in the NDAs. This eliminates the need to

dispose construction waste to public fill 1'eception facilities and landfills.

As we a1'e currently carrying out ground investigation wo1'ks to

determine the distribution and volume of arsenic-containing soil in KTN NDA,

the 1'esults would only be available afte1' completion of all the investigation

works. We do not have the information on the volume of soil t1'eatment in

KTNNDA.

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The land of the Fanling Golf Course has been held by the Hong Kong Golf Club under Private Recreational Lease (PRL) since 1930, the term of which will expire in 2020. The Home Affairs Bureau (HAB) is conducting the overall PRL Policy Review. Based on the current progress, HAB aims to report findings of the PRL Policy Review to the Panel on Home Affairs of the Legislative Council within 2017 and conduct public/stakeholder consultations thereafter. Nevertheless, the planning and engineering study, public engagements and various technical assessments are still requi1'ed in case of the development of the land. The time required for the above will not be less than that of the development of the KTN and FLN NDAs. In view of time needed, it is not able to replace the NDAs.

We hope the above will provide Hon CHU Hoi-dick with the information about the projects of his concerns. In view of the u1'gency of the approval fo1' the Block Allocation, we hope the Finance Committee can grant funding app1'oval as soon as possible. We stand ready to p1'ovide further infOlmation in response to Members' enquiries.

Yours since1'e旬，

fo1' Sec1'etary for Devel句pment

Copy to : Secretarγfor Financial Se1'vices & the Treasury Secreta1'y fo1' Labour and Welfa1'e Secreta1'y fo1' Home Affai1's Director of Lands Directo1' of Civil Enginee1'ing & Development

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NEW DEVELOPMENT AREA

FANLING NORTH

SHEUNG SHUI

NEW DEVELOPMENT AREA

KWU TUNG NORTH

LOK MA CHAU

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LOCATION PLAN

BOUNDARY OF FANLING NORTH NEW DEVELOPMENT AREA

East Rail Line

PROPOSED REPROVISIONING / ENHANCEMENT OF EGRETRY SITES

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SHEUNG YU RIVER

27.01.2017

A 25.07.2014 OFFICE NAME CHANGEDW.Y. CHAN P.L. LAI

SIGNED SIGNED

WORKS AT FANLING NORTH NEW DEVELOPMENT AREA

FIRST STAGE SITE FORMATION AND ENGINEERING INFRASTRUCTURE

W K LAU

C Y LO

M T LEUNG

27.01.2017

27.01.2017

PROVISIONALSUBJECT TO AMENDMENT

A3 420MM X 297MM

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DEVELOPMENT DEPARTMENT

CIVIL ENGINEERING AND

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NEW TERRITORIES EAST

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