updated initial environmental examination

166
Updated Initial Environmental Examination November 2018 Philippines: Angat Water Transmission Improvement Project Prepared by the Metropolitan Waterworks and Sewerage System for the Asian Development Bank. This is an updated version of the draft originally posted in July 2014 available on https://www.adb.org/projects/documents/angat-water-transmission-improvement-project-iee.

Upload: others

Post on 18-Dec-2021

6 views

Category:

Documents


0 download

TRANSCRIPT

Page 1: Updated Initial Environmental Examination

Updated Initial Environmental Examination

November 2018

Philippines: Angat Water Transmission Improvement

Project

Prepared by the Metropolitan Waterworks and Sewerage System for the Asian Development Bank. This is an updated version of the draft originally posted in July 2014 available on https://www.adb.org/projects/documents/angat-water-transmission-improvement-project-iee.

Page 2: Updated Initial Environmental Examination

ii

Document history

Initial Environmental Examination

Angat Water Transmission Improvement

ADB/MWSS

This document has been issued and amended as follows:

Version Date Description Created by Verified by Approved by

1 Draft Rustica Romero Maynard Delfin Marissa De Guzman

2 2 Feb 2014 Draft Final Rustica Romero / Delfa Uy

Marissa De Guzman

Marissa De Guzman

3 14 Feb 2014 Final Rustica Romero Delfa Uy Marissa De Guzman

4 1 Mar 2014 Revised Final Rustica Romero Delfa Uy Marissa De Guzman

5 28 Feb 2018 Revised Draft MWSS

Disclaimer:

This initial environmental examination is a document of the borrower. The views expressed herein do not necessarily represent those of ADB's Board of Directors, Management, or staff, and may be preliminary in nature. Your attention is directed to the “terms of use” section on ADB’s website.

In preparing any country program or strategy, financing any project, or by making any designation of or reference to a particular territory or geographic area in this document, the Asian Development Bank does not intend to make any judgments as to the legal or other status of any territory or area.

Page 3: Updated Initial Environmental Examination

i

Contents

I. Introduction 1

1.1. Project Location 1

1.2. IEE Report 3

1.3. IEE Approach and Methodology 3

1.3.1. IEE Scope 3

1.3.2. Rapid Environmental Appraisal and Categorization 3

1.3.3. Identification of Study Area 4

1.3.4. Baseline Data Collection 4

1.3.5. Impact Assessment and Mitigation 4

1.3.6. Environmental Management Plan 4

1.3.7. Public Consultation 4

II. Policy, Legal and Administrative Framework 6

2.1. National Policy and Regulatory Framework 6

2.2. ADB Environmental Assessment Requirements 9

III. Project Description 11

3.1. Project Rationale 11

3.1.1. Water Supply and Demand 11

3.1.2. Existing Transmission System Needs and Rehabilitation 14

3.1.3. Transmission System Rehabilitation 17

3.2. Project Alternatives 19

3.2.1. Project fixed parameters 19

3.3. Construction Alternatives 20

3.3.1. Tunnel Construction Methods 20

3.3.2. Table 9:Assessment of tunnel construction methods 21

3.3.3. Cofferdam Options 23

3.4. Project Development Plan and Project Components 24

3.4.1. Tunnel 25

3.4.2. Intake Structure 27

3.4.3. Outlet Structure 27

3.4.4. Channel 27

3.4.5. Construction Support Facilities 30

3.5. Project Duration and Schedule 31

IV. Description of the Environment 32

4.1. The Land 32

4.1.1. Topography and Soils 32

4.1.2. Geology 34

4.1.3. Ecological Resources 35

Page 4: Updated Initial Environmental Examination

ii

4.2. The Air 40

4.2.1. Air Quality 40

4.2.2. Noise Level 43

4.3. Water 46

4.3.1. Climate 46

4.3.2. Seismology 47

4.3.3. Hydrology and Surface Water Resources 47

4.3.4. Groundwater 53

4.3.5. Freshwater Ecology 53

4.4. People 56

4.4.1. Population and Communities 56

4.4.2. Health Facilities 58

4.4.3. Education Facilities 58

4.4.4. Socio-economic Conditions 58

4.4.5. Physical Cultural Resources 59

4.4.6. Historical Background and Unexploded Ordnance (UXO) 59

4.4.7. Indigenous People 60

4.5. Summary Description of the Project Segments 61

V. Potential Impacts and Mitigation Measures 64

5.1. The Land 64

5.2. Air 67

5.3. Water 69

5.4. People 73

VI. Environmental Management Plan 76

6.1. Introduction 76

6.2. Environmental Mitigation Plan 76

6.3. Institutional Arrangement 91

6.3.1 Existing Arrangement 91

6.3.2. Proposed Arrangements for Environmental Management 92

6.3.3. Implementation Schedule 96

6.4. Environmental Monitoring Plan 98

6.4.1.` Monitoring Mechanism 99

6.4.5. Reporting 107

VII. Public Consultation, Information Disclosure and Grievance Redress Mechanism 108

7.1. Public Consultation 108

7.2. Information Disclosure 119

7.3. Additional Public Consultation and Information Campaign 119

7.4. Grievance Redressal Mechanism 120

7.4.1. Informal Approach 120

Page 5: Updated Initial Environmental Examination

iii

7.4.2. Formal Approach 120

VIII. Conclusions and Recommendations 123

References 151

Page 6: Updated Initial Environmental Examination

iv

List of Figures

Figure 1: Location Map ....................................................................................................................................................... 1

Figure 2: Segments of Tunnel 4 Project Component .................................................................................................... 5

Figure 3: Manila water demand with and without 15% buffer ................................................................................ 12

Figure 4: Ipo-La Mesa Transmission System Schematic Diagram ........................................................................... 16

Figure 5: Proposed Transmission System ..................................................................................................................... 18

Figure 6: Tunnel 4 and the MWSS ROW ...................................................................................................................... 20

Figure 7: Tunnel Profile ................................................................................................................................................... 26

Figure 8: Inlet Structure ................................................................................................................................................... 28

Figure 9:Outlet Structure ............................................................................................................................................... 29

Figure 10: Temporary Spoil Disposal Area .................................................................................................................. 30

Figure 11: Projected Tunnel Geology and Ground Elevation ................................................................................... 33

Figure 12: Geology in the Study Area ........................................................................................................................... 35

Figure 13: Surface Water Quality and River Ecology Sampling Stations at Ipo Watershed ............................... 47

Figure 14: Average Turbidity Level at Ipo Dam ....................................................................................................... 48

Figure 15: Surface Water and Groundwater Sampling Stations along Tunnel Segments................................... 52

Figure 16. Guerrilla site map and project site ............................................................................................................. 60

Figure 17: Project Segments ............................................................................................................................................ 62

Figure 18: Location of the Inlet and Associated Works .............................................................................................. 63

Figure 19: Location of the Outlet Structure ................................................................................................................. 64

Figure 20: MWSS Corporate Office Organizational Structure ................................................................................ 91

Figure 21 PMO-AWTIP with Consulting Firm ............................................................................................................ 92

Figure 22: Grievance Redress Mechanism Diagram ................................................................................................ 122

Page 7: Updated Initial Environmental Examination

v

List of Tables

Table 1: Other Relevant Laws, Regulations and Guidelines ................................................................................. 7

Table 2: MWSS Water Permits ....................................................................................................................................... 11

Table 3: MWSS Water allocation.................................................................................................................................... 11

Table 4: Water Available to MWSS from Angat Reservoir ....................................................................................... 11

Table 5: Treatment plant capacities and average volumes (Nov 2012-Jan 2013) ................................................... 13

Table 6: Calculated capacities of conveyances ............................................................................................................ 14

Table 7: Priority for potential rehabilitation to conveyance structures .................................................................. 17

Table 8: Projected flows after rehabilitation................................................................................................................ 19

Table 9: Assessment of tunnel construction methods .......................................................................................... 21

Table 10: Assessment of cofferdam options ................................................................................................................. 24

Table 11: Indicative Construction Program .................................................................................................................. 31

Table 12: Borehole Sediment Quality .......................................................................................................................... 32

Table 13: Ambient Air Quality Results ........................................................................................................................ 42

Table 14: Noise Level Monitoring Results at MWSS Property Brgy. Bigte (Wet Season) ................................... 43

Table 15: Noise Level Monitoring Results at MWSS Property Brgy. Bigte (Dry Season) ................................... 44

Table 16: Noise Level Monitoring Results at Brgy. Hall San Mateo (Wet Season) .............................................. 45

Table 17: Noise Level Monitoring Results at Brgy. Hall San Mateo (Dry Season) .............................................. 45

Table 18: Projected Temperature and Rainfall Change in Bulacan Province (Seasonal increase in

temperature and rainfall) ................................................................................................................................................. 46

Table 19: Projected Temperature and Rainfall Change in Bulacan Province (Frequency on Extreme Events)

.............................................................................................................................................................................................. 46

Table 20: Surface Water Quality in Angat River (Upstream and Downstream of Ipo Dam) ................................. 48

Table 21: Surface Water Quality in Bigte River and Sta. Maria River ................................................................. 50

Table 22: 2013 Borehole and Water Table ..................................................................................................................... 53

Table 25: River Ecology Sampling Stations ................................................................................................................ 54

Table 26: Municipal Profile of Norzagaray, Bulacan ................................................................................................. 57

Table 27: Population/Growth Rate of Norzagaray, Bulacan ..................................................................................... 57

Table 29: Sectoral Distribution of Employment CY 2000, Bulacan and Norzagaray ............................................ 58

Table 30: Extent and Average Yields of Agriculture Land Use: Norzagaray.......................................................... 59

Table 31: Potential Impacts on Land ............................................................................................................................. 64

Page 8: Updated Initial Environmental Examination

vi

Table 32: Potential Impacts on Air ................................................................................................................................. 67

Table 33: Potential Impacts on Water ............................................................................................................................ 70

Table 34: Potential Impacts on People .......................................................................................................................... 73

Table 35: EMP prior to Construction Phase ................................................................................................................ 77

Table 36: EMP for the Construction Phase ................................................................................................................... 79

Table 37: EMP for the Operations Phase ..................................................................................................................... 90

Table 38: Institutional Responsibilities ..................................................................................................................... 94

Table 39: Environmental Management Implementation Schedule ..................................................................... 96

Table 38: Composition of the Multipartite Monitoring Team ................................................................................ 100

Table 39: Environmental Monitoring Plan .................................................................................................................. 102

Table 40: Summary of Public Consultation 2013 July and 2014 July ..................................................................... 108

Table 41: Summary of Public Consultation – 2016 August ..................................................................................... 109

Page 9: Updated Initial Environmental Examination

vii

List of Abbreviations

Page 10: Updated Initial Environmental Examination

viii

AS Atomic Absorption Spectrometry

ADB Asian Development Bank

ADSDPP Ancestral Domain Sustainable Development and Protection Plan

AFP Armed Forces of the Philippines

AQ Aqueduct

AP Affected Person

D&B Design and Build Contractor

Brgy Barangay

BH Borehole

BOD5 Biological Oxygen Demand (5 Days)

CADT Certificate of Ancestral Land Domain Title

CBFM Community-based Forest Management

CEMMP Contractor’s Environmental Management and Monitoring Plan

CITES Convention on International Trade on Endangered Species of Wild Fauna and Flora

CNC

COD

Certificate of Non-coverage

Chemical Oxygen Demand

CLUP

CPDO

Comprehensive Land Use Plan

City Planning and Development Office

CPF Common Purpose Facility

CWA Contractor’s Work Area

DAO Department Administrative Order

D&B

DBH

Design and Build

Diameter at Breast Height

DED Detailed Engineering Design

DENR CO DENR Central Office

DENR MO DENR Memorandum Order

DPWH Department of Public Works and Highways

DOST

DS

Department of Science and Technology

Downstream

DQP

ECA

ECC

Design Quality Plan

Environmental Critical Area

Environmental Compliance Certificate

ECP

EMB

Environmental Critical Project

DENR Environmental Management Bureau

EMP Environmental Management Plan

EO Executive Order

EU Environmental Unit

FED

FGD

Fire and Explosives Division

Focus Group Discussion

FIDIC Fédération Internationale Des Ingénieurs-Conseils (International Federation Of Consulting Engineers)

Page 11: Updated Initial Environmental Examination

ix

FVR Friendship Village Resources

GOP

HH

Government of the Philippines

Household

IEC

IEE

Information, Education and Communication

Initial Environmental Examination

IP Indigenous People (Dumagat)

IUCN International Union for Conservation of Nature

IRA

IV

LGU

Internal Revenue Alignment

Importance Value

Local Government Unit

LWUA Local Water Utilities Administration

Mbg Meters Below Ground

MENRO

MMT

Municipal Environmental and Natural Resources Office

Multipartite Monitoring Team

MOA Memorandum of Agreement

MWCI Manila Water Company Inc.

MWSI Maynilad Water Services Inc.

MWSS Metropolitan Waterworks and Sewerage System

NCIP National Commission on Indigenous Peoples

NCSO National Census and Statistics Office

NGA

NIPAS

National Government Agencies

National Integrated Protected Area System

NPC National Power Corporation

NVH North Village Housing

NWRB National Water Resources Board

O&M

PMO-AWTIP

Operation and Maintenance

Project Management Office for Angat Water Transmission Improvement Project

PA Protected Area

PAGASA

PAMB

PAWB

Philippine Atmospheric Geophysical and Astronomical Services Administration

Protected Area Management Board

Protected Areas and Wildlife Bureau

PCR Physical Cultural Resources

PD Presidential Decree

PGA Peak Ground Acceleration

PNP

PO

Philippine National Police

People’s Organization

Page 12: Updated Initial Environmental Examination

x

PPTA Project Preparation Technical Assistance

QMP

RA

Quality Management Plan

Republic Act

RCE Riparian Channel Evaluation

REA Rapid Environmental Assessment

ROW Right of Way

SAPA Special Use Agreement in the Protected Areas

SPS 2009 ADB Safeguard Policy Statement, June 2009

SPSC

TA

Scoping/Procedural Screening Checklist

Technical Assistance

US Upstream

WHO World Health Organization

WVF West Valley Fault

DQP Design Quality Plan

QMP Quality Management Plan

Page 13: Updated Initial Environmental Examination

xi

Executive Summary

The Angat Water Supply Transmission Improvement Project (AWTIP) seeks to improve the reliability and security of the raw water transmission system through partial transmission system rehabilitation from Ipo to La Mesa and the implementation of water safety, risk and asset management plans. As part of the project, it is proposed to build a new tunnel to augment the water conveyance capacity provided by the three existing tunnels. Once completed, it is possible to drain and inspect each of the tunnels and assess the need for further works.

The Project has been categorized by ADB as environment category B and this IEE was prepared consistent with the environmental assessment requirements of ADB’s Safeguard Policy Statement of 2009 (ADB SPS).

The original IEE was prepared and approved in 2014. The approved IEE is further updated for the changed in tunnel methodology from Drill and Blast to Tunnel Boring Machine (TBM). The used of TBM technology during excavation is to avoid blasting and to minimize dust.

The proposed Tunnel 4 will be 6.4km in length and 4.2 m in clear internal diameter and 4.94m external diameter and lying adjacent to the existing tunnel 1. The tunnel will be located at about 100m to 150m below ground surface with maximum depth of 200m. The depth at the inlet and outlet is about 10m and 8m, respectively.

It will use a mechanized excavation method with a double shield Tunnel Boring Machine (TBM). In the first stretch, just downstream of intake, the alignment is characterized by two curves with a radius of 350m and a length of 780m to allow the TBM excavation, the two curves are followed by a straight stretch with a length of roughly 5,660m, thus attaining a total length of 6,440m. The mechanical excavation will proceed from the outlet portal at Bigte towards the intake at Ipo Reservoir, where the TBM will be dismantled. Construction of access road for TBM assembly at the Outlet Portal will be done by stabilizing the existing slope and deep excavation up to the invert level of the new tunnel and the construction of TBM launching chamber.

Permanent access roads will be constructed also along the Inlet Portal Area with a total length of 865 meters inside Ipo Dam area; this road will also be used as Construction Working Area (CWA) going to Tunnel Intake.

Slope stabilization will be assured with the following works, mortar injection with cement mortars, micropile wall with anchors will be used as reinforcement to establish the vertical cut of the slope and to be reinforced by soil nails secure with wire mesh and shotcrete. The intake will be located between the new and old Ipo dams. The intake structure will comprise a rectangular basin, with a trash rack to control debris entering the tunnel and stop logs for closure and control of sluice gates to regulate the flow of water in the tunnel.

Traffic and Transportation Management Plan shall be prepared for the site access roads including IPO roads to ensure that no hazards would result from the increased truck traffic and that traffic flow would not be adversely impacted.

The few impacts of high magnitude (without mitigation) during construction will not be distinct. Tunnel 4 will be the fourth tunnel to be constructed in the MWSS ROW. These impacts will not be sufficient to threaten the surrounding resources. During operation, low to moderate impacts will come from maintenance and repair.

An environmental management plan (EMP) was developed to provide specific actions deemed necessary to assist in mitigating the environmental impacts, guide the environmentally-sound execution of the proposed project, and ensure efficient lines of communication between the implementing agency, project management unit, consultants, and contractors. The EMP also provides a proactive, feasible, and practical working tool to enable the measurement and monitoring performance on-site.

Two types of monitoring are required: environmental and compliance. Environmental monitoring evaluates the residual impacts of construction and operation activities in the environment and as necessary modifies the mitigation measures to ensure its effectiveness. Compliance monitoring ensures that all parties comply with the environmental requirements as set under Philippine legislation and policies, and the requirements described in this updated IEE and Contractor’s

Page 14: Updated Initial Environmental Examination

xii

CEMP. The hierarchy of compliance monitoring includes monitoring activities conducted by the Contractor, CPF internal monitoring and MWSS, MMT external monitoring, DENR, ADB and an independent monitoring team. The proposed Environmental Monitoring Plan covers water quality, air quality, noise, and vegetation clearance. It also includes key parameters, sampling methodology and testing. The monitoring plan is focused on the construction period as no significant impact was identified during the operation phase. The Environmental Monitoring Plan will be updated as needed.

Series of Public consultations were held within the communities of Brgys. San Mateo and Bigte including Dumagats in Ipo Watershed. The consultations aim to provide information on the updates of the proposed projects particularly the change in methodology (DBM to TBM). Stakeholders such NHCP, NIA, NWRB, PAGASA, MWSS, DENR, NPC, NCIP, the EIA RevCom, LGUs and POs.

The program’s grievance redressal mechanism provides the citizens with a platform for redressal of their grievances and describes the informal and formal channels, time frame, and mechanisms for resolving complaints about environmental performance. The project implementation will require a Project Management Office (PMO). For this project, a consulting firm will oversee the implementation of the Environmental Management Plan, including the mitigation measures and environmental monitoring program identified in the EMP and the compliance of the Contractor with its CEMMP.

The updated IEE concludes that most of the environmental impacts associated with the Tunnel 4 are expected to arise during construction. Potential impacts will be localized and site-specific. Most of the identified impacts are low and temporary and if assessed adversely, it can be mitigated to an acceptable level without difficulty through standard site, engineering and construction practices. No significant adverse impacts have been identified during operation phase.

Page 15: Updated Initial Environmental Examination

1

I. Introduction

This report presents the updated Initial Environmental Examination (IEE) of the Angat Water Transmission Improvement Project (AWTIP) which aims to improve reliability of water supply in Metro Manila. The project is located in Bulacan Province (Luzon Island), about 35km northeast of Manila (Figure 1). Metropolitan Waterworks and Sewerage System (MWSS), the project proponent, is seeking a loan from the Asian Development Bank (ADB). This updated IEE has been prepared to comply with ADB environmental safeguard requirements.

1.1. Project Location

The project is located in Brgys. San Mateo and Bigte in the Municipality of Norzagaray, Province of Bulacan, which is about 35km northeast of Manila. The project will involve the construction of about 6.4km long, 4m in diameter tunnel that will be used to transmit raw water from Ipo reservoir to MWSS Bigte Portal. The underground tunnel will be about 50mbg to 200mbg and its alignment will be within the existing MWSS Tunnel ROW.

The tunnel alignment will traverse about 6km length in Brgy San Mateo and only about 400m is within Brgy Bigte. The alignment will traverse boundaries of two watersheds in Brgy San Mateo- the Ipo Watershed, which is managed by DENR and MWSS; and Angat Watershed, a declared protected area and bird area, which is managed by NPC. The intake will be at the IPO Dam compound in Brgy. San Mateo, Municipality of Norzagaray at 14° 52’ 25.30” N, 121° 8’ 56.01” E. This location is between the old and new Ipo dam structures. The intake is at relative elevation of 95.7m, nearly 5m below the normal and operating reservoir.

The tunnel alignment will be from 14° 52’ 22.97” N, 121° 8’ 53.34” E in Ipo Dam Compound traversing straight to MWSS Bigte portal at 14° 51’ 31.71” N, 121°5’ 29.35” E. This alignment is within the MWSS existing 60m width tunnel ROW. The outlet will be at the MWSS in Brgy. Bigte at approximately 92.3m relative elevation. The inlet and outlet sites can be accessed through the Ipo Road from Quirino Highway. The area is generally characterized to have rolling terrain and has rural setting. The topography is relatively flat only at Bigte Portal.

Figure 1: Location Map

MWSS Bigte Portal

Angat Dam

Ipo Dam

Page 16: Updated Initial Environmental Examination

2

Photo 1: Location of Tunnel 4 Inlet, CWA and temporary spoil disposal

During construction phase, the Contractor’s work areas and temporary spoil disposal site at Brgy.

Bigte will be within the MWSS compound in Brgy.Bigte (Photo 2 and 3).

Photo 2: Location of temporary spoil disposal in Brgy Bigte

Inlet CWA

Page 17: Updated Initial Environmental Examination

3

Photo 3: Location of CWA near the oulet

1.2. IEE Report

This updated IEE Report covers the details of the initial environmental assessment of the new Tunnel 4 utilizing TBM tunnel methodology from Ipo to Bigte in Norzagaray, Bulacan and associated intake and outlet works. The proposed tunnel construction is considered a priority scheme for the transmission system based on the assessment report. Once constructed, it will facilitate the subsequent rehabilitation of the whole transmission system identified in the assessment report.

1.3. IEE Approach and Methodology

1.3.1. IEE Scope

The IEE is focused on identifying environmental issues in the study area, potential environmental impacts and risks associated with the construction and operation of the proposed project, facilitating mitigation measures, and setting out an outline of the environmental management plan (EMP) to minimize adverse environmental impacts.

The IEE study includes an environmental assessment of the tunnel alignment and related project components such as the Contractor’s work areas, most of which are within the MWSS infrastructure compound; and temporary spoil disposal area. The study was carried out following the ADB SPS 2009 and in reference to the national policy and regulatory framework discussed in Section 2.

1.3.2. Rapid Environmental Appraisal and Categorization

ADB‘s Rapid Environmental Assessment (REA) form was used initially to identify potential impacts. The project has been classified as Category B based on the type of environmental assessment required following ADB safeguard policies, indicating that there are potentially some adverse environmental impacts, but not sufficient to warrant a full environmental impact assessment (EIA).

Page 18: Updated Initial Environmental Examination

4

1.3.3. Identification of Study Area

The optimum location of the tunnel alignment from the inlet through the entire alignment to the outlet has been selected to mitigate the potential impacts of tunnel construction and operation works on air, water, flora and fauna, and within the communities.

The study area extends along the full length of the new tunnel alignment, including the project related sites for the construction on the inlet and outlet works, and the temporary spoil disposal sites.

The tunnel alignment was subdivided into 1km lengths resulting in seven segments for the entire project. The characteristics of the study area and the potential for environmental and social impacts were then assessed in each segment. Segments 1 and 7 at either end of the project include inlet and outlet works, tunnel portal, Contractor’s work areas, and temporary spoil disposal sites. Most of the construction-related impacts are associated with these segments. Segments 2 to 6 lie along the alignment of the tunnel, where there would be limited effects from tunnelling.

1.3.4. Baseline Data Collection

Environmental surveys for surface water quality, ambient air quality, noise, terrestrial (flora and fauna) ecology, and river ecology, were undertaken in the study area. Surveys and interview to the potential affected people were also conducted. Where appropriate, the environmental quality data were compared with the Philippine environmental quality standards, and where national standards were not available, with international criteria. Detailed terrestrial vegetation and fauna surveys were undertaken in Segments 1 and 7, with less detailed surveys along Segments 2 to 6. The data are presented in Chapter IV on the baseline together with secondary data gathered from various government agencies and other related literature. A GIS mapping exercise was undertaken with the various inputs from surveys and existing maps such as topographic maps and hazard maps to characterize the project site.

1.3.5. Impact Assessment and Mitigation

This updated IEE identified the potential adverse environmental impacts along each segment of the tunnel alignment during the construction and operation. These impacts were described qualitatively and proposals for appropriate mitigation put forward.

1.3.6. Environmental Management Plan

The Environmental Management Plan (EMP) was developed further based on the finalized detailed engineering design.

1.3.7. Public Consultation

Public consultation meetings were held with the communities in Brgys. Bigte and San Mateo including Dumagats in Ipo Watershed to solicit their recommendations/suggestions about the project. Information dissemination on the changes on other project components including project status were also presented for transparency and updating among the local residents and all the stakeholders.

Page 19: Updated Initial Environmental Examination

5

Figure 2: Segments of Tunnel 4 Project Component

Segment 1

6 7

Outlet

Structure

Inlet Structure

Segment 2

Segment 3

Segment 4

Segment 5

Segment 6

Segment 7

Page 20: Updated Initial Environmental Examination

6

II. Policy, Legal and Administrative Framework

2.1. National Policy and Regulatory Framework

The following laws/policies cover the framework for environmental assessment in the Philippines:

a) The 1987 Philippine Constitution, Section 16, Article II and Section 15, sets the basic framework for the country’s Policy on Environment, stating: “The State shall protect and advance the right of the people to a balanced and healthful ecology in accord with the rhythm and harmony of nature. The State is mandated to protect and promote the people’s right to health.”

b) Presidential Decrees (PD) 1586, 1978 established the Philippine EIS system, an assessment process through which all projects categorized as environmentally critical or situated within environmentally critical areas are required to undertake.

c) Presidential Decree 1151, 1979 represents the Philippine Environmental Policy, requiring all proponents of projects that significantly affect the quality of the environment to prepare a detail statement on: (i) environmental impacts of the proposed project; (ii) any unavoidable adverse environmental effect of the project when implemented; (iii) alternative to the proposed action; (iv) determination that the short-term uses of the resources of the environment are consistent with the maintenance and enhancement of the long-term productivity of the same; and (v) finding to be made that such use and commitment are warranted, in case a proposed project will involve the use of non-renewable resources.

d) Proclamation 2146, 1981 declared certain types of project and areas as environmentally critical and within the scope of the EIS System. Proclamation No. 803, 1996 added one type of project as environmentally critical.

e) DENR Administrative Order 30 in 2003 (DAO 03-30) sets out the Implementing Rules and Regulations of the Philippine EIS System.

f) Revised Procedural Manual for DAO 03-30, 2008 prescribes the procedures for the processing of applications for Environmental Compliance Certificates (ECCs) and Certificates of Non-Coverage (CNCs).

g) DENR Memorandum Circular No. 2007-08, 2007 segregates the practice of requiring permits, clearances, licenses, endorsements, resolutions and other government approvals under the jurisdictions other National Government Agencies (NGAs) and Local Government Units (LGUs) so as not to pre-empt the EIA evaluation process. As such, the EIA findings and recommendations are transmitted through the ECC for consideration by the NGAs and LGUs in the processing or prior to the issuance of their respective permits/clearances. It stipulates that the issuance of ECC or CNC for a project does not exempt the proponent from securing other government permits and clearances as required by other laws.

h) DENR Administrative Order No. 2016-08, Water Quality Guidelines and General Effluent Standards of 2016, provides guidelines for the classification of water bodies in the country; determination of time trends and the evaluation of stages of deterioration/enhancement in water quality; evaluation of the need for taking actions in preventing, controlling, or abating water pollution; and designation of water quality

Page 21: Updated Initial Environmental Examination

7

management areas (WQMA). In addition, this Order is issued to set the General Effluent Standards (GES).

i) DENR Administrative Order No.2017-15, Guidelines on Public Participation under the Philippine Environmental Impact Statement (EIS) System, improve and rationalize Public Participation under Philippine EIS System and to achieve meaningful public participation.

Other legal environmental issuances most relevant to the Project are presented in Table 1.

Table 1: Other Relevant Laws, Regulations and Guidelines

Law / Regulation / Guideline Year Relevant provisions Remarks

Protected area management

Republic Act No. 7586

The National Integrated Protected Areas System (NIPAS) Act

1992 Proposals for activities that are outside the scope of the management plan for protected areas (PAs) shall be subject to an EIA before they are adopted, and the results thereof shall be taken into consideration in the decision-making process. An ECC is required prior to the actual implementation of such activities. When allowed to undertake activities, the proponent shall plan and institute measures to minimize any adverse effects and take preventive and remedial action when appropriate.

Although the Project is within a PA classified as initial component, the NIPAS may not be applicable because the Ipo watershed does not have an organized Protected Area Management Board (PAMB) for the watershed PA.

The MWSS ROW is included in the management plan of the Angat Watershed Reserve and Forest Range (Pilot), a protected area. Nevertheless, the Project will secure an ECC in compliance to the Philippine EIS System.

DENR Administrative Order No. 17

Rules and Regulations Governing Special Uses within Protected Areas

2007 A Special Use Agreement in the Protected Areas (SAPA) may be issued within PAs except in strict nature reserves and shall be confined only to the management zones of the PA appropriate for the purpose.

Issuance of SAPA is currently suspended. DENR Region 3 has advised that a Memorandum of Agreement (MOA) is applicable for the Project. An initial draft MOA between the National Power Corporation (NPC), MWSS and DENR has been drafted by DENR and the Consultant on 7 November 2013. Copy has been forwarded to MWSS for its review. It is aimed to secure this MOA promptly.

DENR Administrative Order No. 26

Revised Implementing Rules and Regulations of the NIPAS Act

2008 Prohibited acts within protected areas includes:

- (1) destroying and disturbing plants or animals; (2) dumping of wastes; (3) destroying objects of natural beauty or of interest to cultural communities; (4) damaging roads and trails; (5) squatting or occupying any land within; (6) constructing structure without permit; (7) leaving the PA in unsanitary conditions with refuse, debris or depositions in water bodies; and (8) removing or destroying boundary marks or signs.

Project will be implemented within the MWSS ROW. Appropriate measures are recommended I the EMP to ensure such prohibited acts are prevented during construction and operation.

Page 22: Updated Initial Environmental Examination

8

Law / Regulation / Guideline Year Relevant provisions Remarks

Technical Bulletin No. 2013-01:

List of Protected Areas Under NIPAS System

2013 Lists the Angat Watershed and Forest Range (Pilot) among the PAs under the NIPAS.

This has been considered in the feasibility study.

Tree-cutting

Executive Order No. 277, Amending Section 68 of the PD No. 705 (Revised Forestry Code)

1987 - Watershed reserves are included under forest lands in the Revised Forestry Code. Cutting of trees in forest lands without license is a criminal offense.

Tree-cutting permit is not necessary when cutting trees of common species.

DENR Administrative Order No. 21

Revised Guidelines on the Issuance of Private Land Timber Permit/Special Private Land Timber Permit

2000 Tree-cutting permit is required for cutting premium hardwood. Same permit is not required for trees of common species.

Some trees need to be cleared to give way to the construction activities. Some of the affected trees at the outlet area would qualify for a permit. As such, a tree-cutting permit is necessary.

Executive Order (EO) 23 dated 1 Feb 2011

Moratorium on cutting of timber in natural and residual forests

2011 The DENR is prohibited from issuing tree-cutting permits in all natural and residual forests nationwide, except for clearing of ROW by DPWH, site preparation for tree plantations, silvicultural treatment and similar activities, provided that logs derived from the cutting permits shall be turned over to DENR for proper disposal.

Exemptions may be considered if project is a priority by Government of the Philippines (GOP).

Health and Safety

DOLE Department Order No. 13

Guidelines governing occupational safety and health in the construction industry

1998 Provisions on safety rules, including rules in working at hazardous workplace.

This is considered in the EMP.

DOLE: Occupational Safety and Health Standards (as amended, 1989

2013 May

Provision on duties of employers, workers and other persons, safety rules, including rules in working at hazardous workplace.

This is considered in the EMP.

IRR of RA 8294 dated 06 June 1997 Permit for the use of explosives. This is considered in the EMP.

Environment-related clearances/agreements/permits/licenses have emerged as requisite documents to be secured prior to Project implementation, i.e., prior to the issuance of Notice of Award or Notice to Proceed. These are:

a) ECC, which will require the submission of an EIS that is prepared and submitted for approval to the DENR Environmental Management Bureau (EMB) Central Office. An ECC will be required prior to Notice of Award.

An ECC or proof of submission of the Project EIS to the EMB Central Office for processing is a requisite document for ICC clearance/NEDA Board approval for the Project loan.

Proof of submission of EIS to the EMB Central Office for processing is a requisite document for the application of a tree-cutting permit.

Page 23: Updated Initial Environmental Examination

9

b) Tree-cutting permit, which will be secured from DENR RO3 by MWSS as the authorized land user of MWSS ROW. This will be applied for only when the EIS has been submitted to the EMB Central Office for processing; but should have been secured prior to Notice of Award. According to DAO 2000-21, the following documents will be required: (i) letter application; (ii) sketch map of area applied for; (iii) development plan, if application covers 10ha or larger with at least 50% of the area covered with forest trees; (iv) endorsement from any of the following LGU officials, namely: concerned Barangay Chairman, Municipal/City Mayor, or Provincial Governor; and (v) inventory fee based on existing regulations. DENR RO3 advised that the MOA among MWSS, NPC and DENR will be attached to the application as supporting document. In addition to the application requirements, a 100% timber inventory needs to be undertaken by registered forester/s of Region 3 in accordance with the guidelines set in Section 6 of DAO 2000-21.

A proof of submission of the Project EIS to the EMB Central Office for processing will be used as basis for permit issuance.

The key environmental quality standards applied in this IEE include: (i) National Ambient Air Quality Criteria for Pollutants, 1998; (ii) Noise Control Regulations, 1980; and (iii) Water Quality Guidelines and General Effluent Standards of 2016(DAO 2016-08). International standards referred to include the WHO Air Quality Guidelines, Global Update 2005; WHO Guideline for Community Noise, 1999; WB Pollution Prevention and Abatement Handbook, 1998; IFC Environmental, Health and Safety (EHS) Guidelines; and Assessing Vibration: Technical Guide, 2006 in the absence of a national vibration guideline.

The Philippines became part of the following three international environmental agreements most

relevant to the Project: (i) UNESCO World Heritage Convention in 1985, committing to ensure the protection and conservation of the cultural and natural heritage situated on territory of, and primarily belonging to, the State; and (ii) Convention of Biodiversity in 1993, committing to require environmental assessment of projects that are likely to have significant adverse effects on biological diversity with a view of avoiding or minimizing such effects; and (iii) Convention on Wetlands of International Importance especially as Waterfowl Habitat (Ramsar Convention), in 1994, committing to conserve and wisely use wetlands (i.e., maintaining ecological character) as a contribution toward achieving sustainable development locally and worldwide.

2.2. ADB Environmental Assessment Requirements

According to ADB guidelines, the process of determining a project’s environment category is to prepare a rapid environmental assessment (REA) screening checklist, taking into account the type, size, and location of the proposed project. Based on ADB’s Safeguard Policy Statement 2009 (SPS 2009), a project is classified as one of the four environmental categories (A, B, C, or FI) as follows:

Category A: Projects with potential for significant adverse environmental impacts that are irreversible, diverse or unprecedented. These impacts may affect an area larger than the sites or facilities subject to physical works. An environmental impact assessment is required.

Category B: Projects judged to have some adverse environmental impacts, but of lesser degree and/or significance than those for category A projects. Impacts are site-specific, few if any of them are irreversible, and in most cases mitigation measures can be designed more readily than for Category A projects. An initial environmental examination (IEE) is required.

Page 24: Updated Initial Environmental Examination

10

Category C: Projects likely to have minimal or no adverse environmental impacts. No environmental assessment is required although environmental implications are still reviewed.

Category FI: Projects are classified as category FI if they involve investment of funds to or through a financial intermediary. Where the FI’s investment have minimal or no adverse environmental risks. The FI project will be treated as category C. All other FI’s must establish and maintain an environmental and social management system and must comply with the environmental safeguards requirements specified in SPS 2009 if the FI’s subprojects have the potential for significant adverse environmental impacts.

According to Philippines environmental guidelines, the Project can be considered as either under Group II or III while ADB has categorized the Project as environment category B. Hence, this IEE has been prepared to meet the requirements of both the ADB SPS 2009 and the government. Upon ADB’s receipt of the final IEE from MWSS, this will be publicly disclosed through posting on ADB’s website.

Page 25: Updated Initial Environmental Examination

11

III. Project Description

3.1. Project Rationale

3.1.1. Water Supply and Demand

3.1.1.1. Supply

39. The 14 million population of Metro Manila currently depends on the Umiray-Angat-Ipo multipurpose scheme for over 95% of its water supply. There are plans to develop another significant water source through the New Centennial Project currently being studied by MWSS. However, this will only be operational after 2020. The supply of sufficient and wholesome water from the Umiray-Angat-Ipo system is critical to the well-being of the Manila population.

40. MWSS has been granted water permits with a total volume of 54.57 cms.

Table 2: MWSS Water Permits

Water Source

Water Permit Volume Granted (water right)

Angat River No water permit issued; Board Resolution No 02-0389

22 m³/s

Angat River 11462 15 m³/s (from NIA’s Unutilized water)

Umiray River 7359 14 m³/s

Umiray River 14202 3.57 m³/s

TOTAL 54.57 m³/s

41. The MWSS obtained the following water allocation pursuant to NWRB Board Resolution No 016-0806, subject to availability of water, summarized in Table below.

Table 3: MWSS Water allocation

Water Source Water Volume allocation Angat Reservoir 20.1 m³/s

Unutilized water from irrigation 15 m³/s

Umiray-Angat Transbasin Project

10.9 m³/s

TOTAL 46 m

42. The reliable flow available to MWSS from the Angat reservoir is shown in Table, which is based on monthly mean flows from January 2001 to December 2010.

Table 4: Water Available to MWSS from Angat Reservoir Water Source Water Volume allocation

Angat Reservoir 20.1 m³/s

Unutilized water from irrigation 15 m³/s

Umiray-Angat Transbasin Project 10.9 m³/s TOTAL 46 cm

Page 26: Updated Initial Environmental Examination

12

43. In addition to Angat releases, the available flows to MWSS at Ipo are augmented by runoff from the Ipo catchment between Angat and Ipo dams. This contributes an additional average flow of about 2m³/s at Ipo. Clearly, the water made available to MWSS is often below 46m³/s granted water allocation. MWSS plans to develop projects in the coming years so that a flow of 46m³/s can be relied on from the Angat system. At the end of June 2013, MWSS informed that water allocation would be increased by 4m³/s in consideration of the actual flows from Umiray, which are higher than the allocated 9m³/s. However, this additional allocation will be supplied to Bulacan Province from the transmission system. With the unreliability of the current water allocation, it is not clear how this additional allocation will be a secure resource. The 2010 Memorandum of Agreement (MOA) on the Angat Water Protocol provides the allocation of water for irrigation and municipal use to be determined by National Water Resources Board (NWRB) in accordance with the Philippine Water Code. The Angat-Umiray-Ipo supply is augmented by flow from the La Mesa-Alat catchment estimated at an average of 1.4m³/s. Water is also abstracted from Laguna Lake at the Putatan Reverse Osmosis (RO) plant. This has a capacity of 1.15m³/s, which is expected to double in the coming years.

47. Existing water resources could therefore provide up to 51.7 m³/s , if the flow of 46m³/s from Angat

was secure and the relevant treatment plant and distribution infrastructure were constructed. 3.1.1.2. Demand

48. Several demand scenarios are available for the future water requirements in Metro Manila. MWSS and its concessionaires have used these studies, with some adjustments, to agree the demand forecast shown Figure 3. The indicated growth and the 15% buffer are higher than what the World Bank and JICA studies suggest but have been adopted by MWSS and its concessionaires in the on-going rate rebasing.

Figure 3: Manila water demand with and without 15% buffer

49. In addition to the demands of Metro Manila, the transmission system supplies approximately 0.5m³/s of raw water to San Jose del Monte treatment plant and other private customers. There are also many illegal users estimated to consume 0.1m³/s raw water for domestic use with similar quantity for agricultural purposes. At the end of June, we were informed that the Bulacan bulk water supply project currently under study within MWSS is likely to require up to 5.5m³/s from a take-off on the aqueducts at Pleasant Hills, approximately 10.2km from Bigte.

Page 27: Updated Initial Environmental Examination

13

50. These forecasts are relevant to water resource planning, but do not directly affect the transmission system under study, which is limited by the granted water allocation of 46m³/s. There are suggestions that this may be increased by 4m³/s, as the Umiray scheme produces this in addition to the 9m³/s already granted to MWSS. However, given the unreliability of flow releases from Angat, the high risk of continuing to rely on the Angat single source, and the plan to develop the New Centennial Project, this increased flow is not a significant factor in this current design.

51. The current available supplies to meet the demand are approximately 49.4m³/s from Angat, Ipo, La Mesa and Alat catchments, and up to 2.3m³/s from the Putatan RO plant once its capacity is doubled. The New Centennial Water Source Project is set to meet the demands above these and planned to come on stream at about the same time as the ‘demand with buffer’ exceeds the available supply in 2020.

3.1.1.3. Treatment Plant Demand

52. For the Umiray-Angat-Ipo-La Mesa-Alat water sources, Table 5 shows the treatment plant design capacities, average raw water demand and treated water production over three months from November 2012 to January 2013. Currently, raw water demand is approximately 40m³/s while the capacity is approximately 48m³/s. These volumes, along with direct usage from the transmission system, can be made available from the current sources provided the reliability of the Angat system is improved.

Table 5: Treatment plant capacities and average volumes (Nov 2012-Jan 2013)

Capacity m³/s

Demand Capacity MLD

Demand

Raw Water m³/s

Treated m³/s

Raw Water MLD

Treated MLD

MWSI

La Mesa 1 17.4 15.3 14.1 1,500 1,326 1,214

La Mesa 2 10.4 8.6 8.1 900 742 700

Sub Total 27.8 23.9 22.2 2,400 2,068 1,914

MWCI

Balara 1 5.4 3.6 3.6 470 312 307

Balara 2 13.1 11.6 11.3 1,130 1,001 979 Rodriguez (East La Mesa) 1.4 0.5 0.5 120 42 40

Sub total 19.9 15.7 15.3 1,720 1,355 1,326

Total 47.7 39.6 37.5 4,120 3,423 3,240

Page 28: Updated Initial Environmental Examination

14

3.1.2. Existing Transmission System Needs and Rehabilitation

3.1.2.1. Water Transmission System Assessment

53. Water from the Angat River is transmitted from Ipo Dam to Bigte through the three existing tunnels. From Bigte, water is conveyed along six aqueducts (pipelines), with Aqueducts 1 and 2 carrying water to La Mesa reservoir and the remaining four aqueducts carrying water to La Mesa water treatment plant. The existing transmission system has been assessed in three main areas: (1) condition, (2) hydraulic performance, and (3) seismic resilience.

54. Based on the condition assessment, the main pipelines appear in reasonable condition, although the older Aqueducts 1 and 2, 3 and 4 show leakage reaching nearly 10%. This level of leakage will become unacceptable as demand increases with limited water availability. Rehabilitation is likely to involve local repair and/or replacement of longer pipe lengths. The tunnels continue to convey significant volumes of raw water, which indicate that they are intact with no major collapse. To check the actual conditions and extent of remediation needed by existing tunnels, internal access is required. It is anticipated that the unlined tunnel 1 need remediation. A completed Tunnel 4 internal access will be possible without disrupting water supply to Metro Manila and other areas served by the system.

55. The capacity of the various tunnels and aqueducts of the transmission system have been assessed and used to develop an estimate of the hydraulic characteristics of the system. The capacities of the various conveyances using these characteristics are indicated in Table 6.

Table 6: Calculated capacities of conveyances

Water levels

Capacity (m³/s) Effective flow (m³/s)

Ipo Bigte Portal

TUN1 100.3 88.0 6.6 6.6

TUN2 100.3 89.5 17.4 17.4

TUN3 100.3 95.5 19.0 19.0

TUN Total 43.0 43.0

AQ1+2 88.0 80.0 3.1 3.1

AQ3 88.0 80.0 6.8 6.8

AQ4 89.5 80.0 13.3 13.3

AQ5 95.5 80.0 19.0 19.0

Page 29: Updated Initial Environmental Examination

15

Water levels

Capacity (m³/s) Effective flow (m³/s)

Ipo Bigte Portal

AQ6 95.5 80.0 17.2 -

AQ Total 59.4 42.2

56. Estimated capacities highlight two important issues for the transmission system:

57. The capacity of the tunnels is below the anticipated maximum flow of 48m³/s (MWSS water allocation of 46m³/s+ 2m³/s from Ipo catchment below Angat) and needs to be increased in the next few years to meet future demands.

58. The aqueduct capacity is apparently more than the water allocation, but unfortunately only one of Aqueducts 5 and 6 can be supplied to its full capacity by Tunnel 3, reducing the effective capacity to approximately 42.2m³/s. As a result, there is no flexibility in the system to allow closure of a conveyance for maintenance/ rehabilitation.

59. Hence, hydraulically, the first requirement is to construct a new Tunnel 4 to: (i) augment supply to Aqueducts 5 and 6 to their full capacities. After this, it will then be possible to sequentially close and fully inspect the older Tunnels 1, 2, 3 and Aqueducts 1-2, 3, and 4. This will also allow some of the assumptions made in the hydraulic and structural/seismic analyses to be reassessed.

60. The assessment of structural resilience of aqueducts indicates that there are no major issues which need to be urgently addressed. The main concern is damage that will occur at hard/stiff points along the pipeline. It is considered that this risk is best dealt with post-earthquake repair, rather than installation of flexible joints. Such joints would be expensive given the large number of hard/stiff points and large diameter of the pipelines. Maintaining a stock of materials to enable rapid repair is considered to be of better value. Some structural reinforcement of several basins is also suggested.

Page 30: Updated Initial Environmental Examination

16

Figure 4: Ipo-La Mesa Transmission System Schematic Diagram

61. The construction of Tunnel No. 4 is mainly aimed at providing operational flexibility and will not

affect the determination of water allocation for MWSS (for domestic and municipal) and for the

National Irrigation Administration (for irrigation) and for any purpose thereof, as confirmed by

NWRB.

62. Once operational will give MWSS the opportunity to thoroughly conduct investigation and

rehabilitation of the old existing tunnels. At the moment, the capacity of Tunnels 1-3 is 43 m3/s

which is below the anticipated maximum flow of 48m³/s (MWSS water allocation of 46m³/s+ 2m³/s

from Ipo catchment below Angat). The repair of the aqueducts, without the construction of Tunnel

4, will result to closing of any of the tunnels that is in series with respective aqueduct. This

approach will result to water interruption and shortage of water supply to Metro Manila. Tunnel

Page 31: Updated Initial Environmental Examination

17

4 will be constructed to convey raw water while any of the existing tunnels are undergoing

inspection and rehabilitation works.

3.1.3. Transmission System Rehabilitation 63. Assessment of the system identifies the need for:

New tunnel to increase capacity and provide operational flexibility

Internal inspection of conveyances and subsequent rehabilitation as necessary

Rehabilitation/renewal of older structures and appurtenances

64. Suggested priority for these works is indicated in Table 7.

Table 7: Priority for potential rehabilitation to conveyance structures

Priority Conveyance Issues Potential rehabilitation methods

Detail study needed after inspection

1 New Tunnel 4 Critical to increase flow and facilitate subsequent inspection and rehabilitation

Described in this feasibility study

2 Tunnel 3 Critical tunnel, no permanent concrete lining, rock bolts, built in 1992(~ 23-year-old)

Permanent concrete lining - locally or total length, use corrosion resistant rock bolts + additional shotcrete

3= Tunnel 2 Important tunnel, built in 1983 (~ 32-year-old) Optioneered repairs to concrete lining

3= Aqueduct 4 Important aqueduct, leakage at 9%, precast pipes potential seismic risk

Optioneered solution from local joint repair to full replacement of pipes, replace all fittings

4 Tunnel 1 Built in 1939 (~76-year-old tunnel) Additional lining, lining repair to maintain integrity

5 Aqueduct 3 Built in 1969 (~46-year-old), leakage at 10%

Repairs to concrete, replace essential fittings for emergency operation

6 Aqueduct 1-2 Built in 1939 (~76-year-old), leakage at 6%, fittings generally not serviceable

Decommission

65. A schematic diagram of this rehabilitated transmission system is indicated in Figure 5.

Page 32: Updated Initial Environmental Examination

18

66.

Figure 5: Proposed Transmission System

67. The capacities of the existing conveyances after rehabilitation will be the calculated values shown in Error! Reference source not found.TABLE 6 with the probable exception of Tunnel 3 (where a concrete lining could reduce capacity to about 17.6m³/s); Aqueduct 4 (where a smooth lining or steel pipe could increase capacity to about 15.4m³/s); and Aqueducts 1-2 once

Tunnel 1

capacity:

6.6 m³/s

Tunnel 2

capacity:

17.4 m³/s

Tunnel

3capacity:

17.6 m³/s

Tunnel 4

capacity:

19.0 m³/s

Page 33: Updated Initial Environmental Examination

19

decommissioned. Tunnel 4 will feed AQ5 and need a matching capacity of 19.0 m³/s. Proposed flows after rehabilitation are indicated in Table 8.

68. The potential 5.5m³/s supply to Bulacan Province from the transmission system, of which we were advised at the end of June, could in theory be accommodated in this rehabilitated system, although overall flexibility would be reduced. It will also be necessary for MWSS to agree with the concessionaires how this supply will be managed.

Table 8: Projected flows after rehabilitation

Tunnel Capacity (m³/s) Aqueduct Capacity (m³/s) Normal operation

Tun 1 6.6 AQ 3 6.8

Tun 2 17.4 AQ 4 15.4 15.4

Tun 4 19.0 AQ 5 19.0 19.0

Tun 3 17.6 AQ 6 17.2 17.2

Tunnel Total 60.6 AQ Total 51.6

3.2. Project Alternatives

69. Fixed parameters/constraints which define the Tunnel 4 project: a) The disruption to operations of transmission system during construction should be minimal.

b) Tunnel 4 must be within the existing MWSS ROW. This is a 60m wide corridor approximately centered on Tunnel 1

c) Tunnel should not pass over or under existing working tunnels as the risk of collapse and disruption is unacceptable. This means Tunnel 4 is restricted to the corridor between Tunnel 1 and the southern boundary of the MWSS ROW.

d) The scheme must convey 19m3/s design criteria for:

i) Elevation of Ipo reservoir water level at 100.3m

ii) Elevation of Basin 3 (AQ5 start) water level at 95.5m

(iii)Hydraulic roughness of concrete to be taken as 4mm. This is the likely long-term roughness after degradation of the concrete surface

e) Intake to be located between the old and the new Ipo Dams to reduce risks of silt built up in front of intake. Silt levels upstream of the old Ipo Dam are at an approximate elevation of 91m and are increasing by approximately 0.3m a year. In comparison, levels downstream of the old dam are approximately 83m.

Such constraints fix the basic layout of the scheme.

70. No alternative, other than tunnel construction, was considered with the given constraints on project siting. Above ground conveyance system is not applicable due to the rugged terrain of Brgy San Mateo.

Page 34: Updated Initial Environmental Examination

20

Figure 6: Tunnel 4 and the MWSS ROW

3.3. Construction Alternatives

3.3.1. Tunnel Construction Methods

71. Potential tunnel construction methodologies have been assessed in Table 9, however, the Tunnel Boring Machine was considered the Contractor.

Page 35: Updated Initial Environmental Examination

21

Table 9: Assessment of tunnel construction methods

Method Advantages Disadvantages

1 Drill and Blast

(D&B)

Low capital cost of equipment is

likely to make it most cost effective

Shorter mobilization than tunnel

boring machine (TBM)

Known technology

Could work from both faces, giving

flexibility and better programme

certainty

Use of explosives during

construction (safety hazard)

Longer construction program

1.1

Drill and Blast

(D&B) one pass

(i.e. no

secondary lining)

Shorter construction programme

than 1.2

Durability of rock bolts will be a

problem, hence long-term reliability.

Note that double corrosion protection

(DCP) rock bolts could be used, but

handling is an issue during the

excavation support phase.

High hydraulic roughness

1.2

Drill and Blast

(D&B) two pass

with cast in-situ

concrete lining

Better durability than 1.1 or 1.3

Low hydraulic roughness

Longer construction programme than

1.1 or 1.3

Higher capital cost than 1.1 or 1.3.

1.3

Drill and Blast

(D&B) two pass,

with DCP rock

bolts

Better construction programme than

1.2

Better reliability of durability than 1.1

High hydraulic roughness

Poorer durability than 1.2

Page 36: Updated Initial Environmental Examination

22

Method Advantages Disadvantages

2 Tunnel boring

machine (TBM)

TBM boring will cause less disturbance

to the nearby Tunnel 1 than in case of

the drill and blast excavation method.

Double shield TBM, as proposed by the

Contractor, is less subject to slowing

the advance rate when crossing lower

quality rock. Therefore, less probability

that construction period and project

cost being affected by poorer

geological conditions than estimated in

the FS.

excavation speed (shorter

construction program);

work under complete safety

conditions;

versatility of usage in different types

of materials;

possibility to perform consolidations

of the rock in maximum security

reaction time in case of high water

inflow and collapse

ability to overtake faults and

fractured zones.

High capital cost for machinery

Long mobilization (potentially will

need to build a new one, or refurbish

and existing machine)

High power requirements

If TBM stops, all advance stops

Note: that a Contractor might have

appropriate TBM available, in which

case programme and cost

disadvantages could be negated.

installation of primary support is not

immediate but only after the TBM

passage (approx. 8 m from the face

of the tunnel);

impossibility to inspect the front

during excavation;

certain reduction in possible

positions and geometry for soil

treatment.

The following are the main types of

action to mitigate risks within the tunnel

and to ensure the normal progress of

the excavation process:

The TBM shall be provided with

facility for probing ahead of the

tunnel face;

The TBM shall have facility to allow

for the stabilization of the exposed

tunnel surfaces and for controlling

the inflow of ground water and thus

to minimize water drawdown;

Ability to install steel sets and panels

in faulted areas or in zones where

rocks conditions are poor. This

additional safety measure is a further

step on risk’s mitigation as it protects

the working areas and provide

necessary support to the tunnel in

cases where the geological condition

becomes adverse.

Page 37: Updated Initial Environmental Examination

23

Method Advantages Disadvantages

2.1

TBM one pass

with full segment

ring

Low hydraulic roughness

Higher construction advance rate

Will require segment casting yard –

increasing land take and capital cost

2.2

TBM one pass,

with bolts and

sprayed

concrete

No segment casting yard required

Weak ground requiring ribs will

reduce tunnel diameter, and rock

bolt heads will be exposed, resulting

in reduced hydraulic efficiency

Durability of rock bolts will be a

problem, hence long-term reliability

2.3

TBM two pass,

with full segment

lining followed by

cast in-situ

concrete lining

Not worth the increased time and

cost to be viable – the segmental

lining is likely to have a much better

flow performance (even with the bolt

pockets) than sprayed concrete

anyway

2.4

TBM two pass,

with bolts and

sprayed

concrete

followed by cast

in-situ concrete

lining

Overcomes problem of varying

diameter with ground conditions

Overcomes need for segment

casting yard

Extends construction programme

2.5

TBM two pass,

with bolts and

sprayed

concrete

temporary

support, followed

by DCP

permanent bolts

As for 2.2, except durability issue

addressed

Slightly longer construction

programme

3 Roadheader

construction Advantages as for 1 Rock too hard to be viable

3.3.2. Cofferdam Options

72. Various cofferdam or construction options for tunnel portal have been reviewed (Table 10). The purpose of the structural analysis is to determine the tubular sheet pile requirement required for the cofferdam to resist the ground and water pressures during construction. These cofferdam option may be reviewed and considered by the Contractor.

Page 38: Updated Initial Environmental Examination

24

Table 10: Assessment of cofferdam options

Cofferdam type Advantages Disadvantages

Traditional sheet pile (Z type or U type sheet pile)

Simple in handling and sourcing

Low risk in installation Relatively water tight

structure

Lack of structural stability subject to earth pressure in cantilever section

Waling and strut may be required and the working space will be comprised

Won’t take impact loads from waterborne craft – additional protection would be needed

Gabion wall

Utilises local material Relatively cost-effective when

compared to sheet pile in small scale of project

Stable foundation is required for cofferdam to provide overall stability

Significant dredging would be required prior to placing the wall, with resultant turbidity issues

Height and width of the Gabion wall in this case will be significantly cost ineffective

Water leakage could cause adverse effects

Tubular sheet pile

Simple in handling and sourcing

Low risk in installation Can be installed in rock layer

by coring method or pre-drill method

Relatively watertight structure Good in structure capacity for

earth pressure without water or strut for cantilever section

Quiet installation if “press in” machines are used

Can take vertical load, and so could be used to support construction plant or a platform

The pile need to be sourced from overseas

Special machines are required for the coring or pre drill “press in” installation method

Relatively expensive when compared to traditional sheet pile or Gabion wall

Won’t take impact loads from waterborne craft – additional protection would be needed.

Tunnel piercing No cofferdam is required

The tunnel is under flood condition

Lack of space for intake structures

3.4. Project Development Plan and Project Components

73. The proposed scheme will involve the construction of a fourth tunnel (Tunnel 4) and its associated structures, namely: intake structure; outlet structure, and channel connecting Tunnel 4 outlet portal to existing Aqueduct 5.

Page 39: Updated Initial Environmental Examination

25

3.4.1. Tunnel

74. The proposed Tunnel 4 will be 6.4km long and 4.2m in diameter (finished internal diameter), lying within the MWSS ROW and adjacent to Tunnel 1, and running from Ipo reservoir (14° 52’ 22.97” N, 121° 8’ 53.34” E) to Bigte (at 14° 51’ 31.71” N, 121°5’ 29.35” E). Much of the tunnel will be located at depths from 100m to 150m below the ground surface, with a maximum depth of approximately 200m (Figure 7). The tunnel will have a precast concrete lining with steel reinforcement to ensure structural integrity and raw water flows in the long term.

Page 40: Updated Initial Environmental Examination

26

Figure 7: Tunnel Profile

Page 41: Updated Initial Environmental Examination

27

75. Significant consideration has been given to the siting of the new tunnel and portal. The existing MWSS ROW is on average 60m wide and centered on Tunnel 1. MWSS requires that the new tunnel should be within this ROW. The optimum tunnel site would also minimize disruption to the existing operations. Notwithstanding the above, the new tunnel intake should be located in the same general area as the existing intakes. Taking all the constraints into account, the most favourable location for Tunnel 4 intake lies upstream of the existing intakes and in an area where reservoir silting is minimal.

3.4.2. Intake Structure

76. The intake structure provides a conduit between the reservoir and the tunnel inlet portal located between the new and old Ipo Dams (14° 52’ 25.30” N, 121° 8’ 56.01” E). Such structure comprises a rectangular box with nominal dimensions of 10m wide and 18m long. A transition structure, approximately 10m long and 4m wide, allows for transition from the rectangular section to the circular profile at the tunnel. The intake structure invert is set at a relative elevation of 95.7m, nearly 5m below the normal reservoir operating level. The top deck is set at relative elevation of 103.5m. The intake structure includes a trash rack to control debris entering the tunnel, stop logs for closure and control or sluice gates to regulate the flow to the tunnel. The inlet works will be located at the depths of approximately 10m.

3.4.3. Outlet Structure

77. The outlet structure is located at the Bigte end of Tunnel 4 (14° 51’ 31.71” N, 121° 5’ 29.35”E) and provides a transition between the tunnel cross‐section and the channel that carries water to Aqueduct 5. The outlet structure comprises an uncovered rectangular basin 4m wide and 7m long, with an outlet invert elevation at about 92.3m. There is also an observation deck for maintenance and operation. The outlet works will be located at the depths of approximately 8m.

3.4.4. Channel

78. The channel connects (or carries water from) Tunnel 4 outlet portal to the existing Aqueduct 5. Its alignment will generally follow the contour of the hill behind the existing Bigte basins. It is rectangular in section of 4m wide and 4.5m deep

Page 42: Updated Initial Environmental Examination

28

Figure 8: Inlet Structure

Page 43: Updated Initial Environmental Examination

29

Figure 9:Outlet Structure

Page 44: Updated Initial Environmental Examination

30

3.5. Construction Support Facilities

79. Construction support facilities include CWAs and temporary spoil disposal area at the inlet and outlet

3.5.1. Contractor’s Work Area (CWA)

80. CWA is a piece of land that is not contiguous to the project footprint but is necessary to secure project offices, emergency first-response station, construction materials storage, explosive storage, equipment parking, and some necessary pre-fabrication and maintenance works. Outside the Project Offices, sanitation facilities, water supply systems, lighting and internal accesses will be provided for the other activities and works. The explosive storage area should be located and constructed in accordance with Rule 19 of the IRR of RA 8294.

Preliminary CWA sites have been identified:

i) In Segment 1, one CWA site near the intake structure. Access to the CWA will be on

the landside through an existing narrow dirt road and on the waterside by using a barge.

The existing dirt road will be widened under the project to facilitate mobility of workers

and materials during construction.

ii) In Segment 7, two CWA sites near the outlet. Access will be through an existing

concrete road.

3.5.2. Temporary Spoil Disposal Area

81. Temporary spoil disposal area is a staging area for debris, spoils and residual soils from construction works. The temporary disposal area is at the MAPOL Quarry Site. The area has an approximate land area of 4 hectares, located at about 2km southeast from the MWSS Bigte Compound where outlet is located and source of the spoil. A river was found 300m southeast from the site. There is a community within 50m radius of the temporary disposal site.

Figure 10: Temporary Spoil Disposal Area

Page 45: Updated Initial Environmental Examination

31

3.5.3. Ipo Road

82. The Ipo road is a two-lane concrete road from Bigte to Ipo dam Compound. It has sections that are winding; hence additional road signs along the road are needed as precautionary and safety measures. From site visit, the road is in good condition.

3.6. Project Duration and Schedule

83. Tunnel 4 is about 52-months, including 3.5 years for tunnel construction and 12-month defects notification period.

Table 11: Indicative Construction Program

Page 46: Updated Initial Environmental Examination

32

IV. Description of the Environment

4.1. The Land

4.1.1. Topography and Soils

83. Brgy. San Mateo of the Municipality of Norzagaray, where the greater part of the alignment is located, is characterized by hilly to mountainous terrain whose elevation varies from 85masl to 250masl. Brgy. Bigte is characterized by a combination of flat to gently sloping areas and hilly lands with highest elevation of about 95masl.

84. The projected tunnel depth in Brgy. San Mateo is about 200m to 600mbelow ground (mbg) while in Bigte, the tunnel is at 50mbg.

85. Borehole samples were tested for heavy metals to determine if the excavated material which will be disposed in temporary spoil disposal sites may be above sediment quality standard. Adopted criteria used are based on the Thai Environmental Regulation for Habitat and Agriculture as there is no standard established in the Philippines. The results show the rock samples are within standards for heavy metals in soil.

Table 12: Borehole Sediment Quality

Sample code Unit Adopted criteria

BH 3 BH4 BH5

Sampling date 20 July 2013 20 July 2013 20 July 2013

Depth (m) 15.5-17 31-32.5 27.5-29

Segment location

Segment 1 Segment 4 Segment 7

Cadmium mg/kg 37 ND ND 0.3

Chromium mg/kg 300 5.7 9.7 11

Copper mg/kg 1,560 196 106

Iron mg/kg 84,400 30,900 2,140

Lead mg/kg 400 12 19 10

Manganese mg/kg 1800 371 576 48

Nickel mg/kg 1600 9 15 12

Zinc mg/kg 63 63 8.5

Page 47: Updated Initial Environmental Examination

33

Figure 11: Projected Tunnel Geology and Ground Elevation

Page 48: Updated Initial Environmental Examination

34

4.1.2. Geology

4.1.2.1. Ipo Dam

86. The dam site is underlain by the eocene-oligocene Bayabas Formation, an extensive bedded sequence of highly indurated sandstone, shale, chert and pyroclastics mainly agglomerate and welded tuff, and volcanic flows predominantly amygdaloidal basalt with associated minor andesite pillows sometimes framed by chert materials. Surface geology comprises agglomerates and basalts which are hard enough to form abutments for a concrete gravity dam though may require some grouting.

4.1.2.2. Ipo Inlet

87. The area around the Ipo inlet is underlain by the Bayabas Formation or specifically by the massive agglomerate and basalt which was observed to be hard to very hard when fresh. In situ weathering is slight to moderate with residual soil approximated to be no more than a meter deep, except when overlain by talus materials. Various fracture orientations with utmost two joint sets plus random could be present. Except for localized faults/shears, the tunnel will be in good ground with rock mass rating more than 50%.

4.1.2.3. Proposed Tunnel 4 Alignment

88. Tunnel 4 alignment passes through the Buenacop limestone upper member of the Madlum Formation, hence traverses for the most stretch of the tunnel in the middle part of same formation labeled as Alagao volcanics before going into the equally hard Bayabas Formation composed of agglomerate and basalts.

89. The area is underlain by the Bayabas Formation or specifically by the massive agglomerate and basalt which was observed to be hard to very hard when fresh. Joint set spacings could be from 1m to 2m. In situ weathering is slight to moderate with residual soil approximated to be no more than a meter deep, except when overlain by talus materials. Various fracture orientations with utmost two joint sets plus random could be present.

90. Except for localized faults/shears, the tunnel will be in good ground with rock mass rating more than 60%. Estimated rock quality categorized into good, moderate and bad rock could be 50%, 25% and 25%, respectively. No major problems are envisaged during tunnelling, this being the fourth tunnel to be constructed along this corridor. Expected groundwater flow can be relatively dry to moderate inflow.

Page 49: Updated Initial Environmental Examination

35

Figure 12: Geology in the Study Area

4.1.2.4. Tunnel 4 Outlet at Bigte

91. The tunnel outlet at Bigte will be hard and massive limestone with fracture spacings more than 2m. Rock mass rating will be more than 60%, which means the rock material is a very good quality rock.

4.1.2.5. Bigte Interconnecting Basins

92. Like Tunnel 4 outlet, the lithology is limestone with minimal soil cover of no more than 2m. The soil profile is characterized by gravelly/bouldery silt with some clay and sand transported soil if not moderately weathered limestone. Groundwater levels are quite deep of more than 5m.

4.1.3. Ecological Resources

93. Flora and fauna surveys, including river ecology survey, have been carried out to characterize the project location in terms of ecological resources for each of the segments discussed in Section 1 of this report. Segments 1-7 are initially delineated as the direct impact areas.

4.1.3.1. Protected Areas

94. The MWSS tunnel ROW at the Ipo dam segment lies within the indicative boundaries of the Angat Watershed Forest Reserve and the Angat Watershed and Forest Range (Pilot) in the Ipo watershed. The Angat Watershed Forest Reserve, which covers about 55,707ha, is managed by National Power Corporation while the Angat Watershed and Forest Range and the Ipo watershed are managed by MWSS. The Angat Watershed Forest Reserve and the Angat Watershed and Forest Range are considered protected areas under Republic Act (RA) 7586, which is the National Integrated Protected Area System (NIPAS) Act.

Page 50: Updated Initial Environmental Examination

36

4.1.3.2. Terrestrial Ecology

4.1.3.3. Flora

95. Habitats in Segments 1 to 7 are a combination of brushland and agro-ecosystems, dominated by common fruit trees such as mango, santol, caimito and banana, interspersed by residential houses and other built-up areas such as community infrastructure sites. Segment 1, where the intake structure and temporary CWA will be located, is within the boundaries of the Angat Watershed and Forest Reserve, which is a protected area and the site where inlet structure will be located. Hence, a more detailed survey was carried out.

96. In Segment 1, a total of 75 species were recorded, of which 38 were classified as trees, 16 shrub species, 20 herbaceous species and 1 bamboo species. From the total, 18 are agricultural crops and the rest are brushland species with two to three species forest/timber species. Of the tree species, 12 are agricultural crops and the rest of the trees are pioneer species common in brushland and other secondary vegetation.

97. The vegetation in Segment 1 is co-dominated by bamboo known as buho alongside with agricultural crops like mango, coconut, banana and caimito and some other tree pioneers associated with secondary vegetation such as binunga and alagasi. Some forest trees like Taluto (Pterocymbium tinctorium), a medium diameter tree, were also recorded but only a few were found.

98. In Segments 2 to 7, a total of 69 species were recorded, of which 44 were classified as trees, four shrub species, 18 herbaceous species and three bamboo species. From the total, 20 species were either agricultural crops (17 species) or tree plantation crop (three species).

99. As the area is an agro-ecosystem type, the vegetation is expectedly dominated by agricultural crops like mango, coconut, banana and caimito. The areas under fallow and currently non-cultivated areas are dominated by brush and weed species such as alim, binunga, hagonoy and dita, among others.

Photo 4: Raintree and Mahogany-Dominated Vegetation in Bigte Proposed as Contractor’s Work Area

Page 51: Updated Initial Environmental Examination

37

Photo 5: Tree-Dominated Vegetation (Raintree and Balete) in Bigte Tunnel Outlet

Photo 6: Brushland Vegetation in Segment 2

Photo 7: Residential Subdivision and Cultivated Area cum Brushland in Segment 3

Page 52: Updated Initial Environmental Examination

38

Photo 8: Brushland Vegetation in Segment 7 above the Tunnel Outlet in Bigte

Photo 9: Open-type Vegetation in Bigte Proposed for Contractor’s Work Area

100. One threatened species was recorded such as narra (Pterocarpus indicus) classified as

vulnerable by the IUCN. Three individuals with diameters of 80cm, 221cm and 248cm were found in the MWSS Bigte Portal.

4.1.3.4. Fauna

101. Birds. A total of 470 individuals representing 60 species of birds were recorded during transects across the five sampling sites. At least 33 species are non-endemic resident breeders, whereas 21 species are endemic to the Philippines. Also, at least four species are considered as restricted to Luzon Island, namely: the Luzon Tarictic (Penelopides manillae), scale-feathered Malcoha (Phaenicophaeus cumingi), red-crested Malcoha (Phaenicophaeus supercillosus), and the gray-backed tailorbird (Orthothomus derbianus). Most endemic species recorded are strongly associated (with highest abundance) with forest habitats, especially at Segment 1 (CWA, Site 1), Isla Puting Bato where vegetation is dominated by early to mature second-growth forest; these sites have 13 and 12 endemic species, respectively. The proposed spoil disposal area (Site 2) and Isla Puting Bato (Site 3) have isolated aggregates of early second growth forest (mostly dominated by pioneer plant species) and expectedly would harbor a substantial number of endemics as well (nine and seven species, respectively). Segments 5-6 (Site 4) has only two species of endemics and the rest of its avian diversity are strongly associated with open habitats.

Page 53: Updated Initial Environmental Examination

39

102. Mammals. From mist-netting, trapping, ocular evidences, and interviews with local guides, a total of 12 species of mammals were recorded in all five sampling sites (see Appendix 5). This total comprised of four species of bats, four species of rodents, one macaque, and one civet. Two mammal’s species are considered as endemics, the Musky fruit bat (Ptenochirus jagori), and an unidentified shrew rat of the genus Chrotomys (captured by hand at Ipo CWA). Five species are considered as residents, including the three species of bats (Cynopterus, Rousettus, and Tylonycteris), and the macaque Macaca fascicularis (known to occur at Ipo CWA, Isla Puting Bato and MWSS Bigte Portal), and the Palm Civet (Paradoxurus hermaphroditus) whose presence was based on fecal matter seen at Sites 1 and 5. The three invasive pest species recorded were all rodents, and are known to inflict damage to crops, reside in houses and adjacent vegetation, and carry infectious diseases such as Leptospirosis. Virtually all of these invasive, pest rodents occur at all the five sampling sites.

103. Amphibians and Reptiles. A total of five species of amphibians and seven species of reptiles were recorded within the four sampling sites. No survey was done along Segments 5 to 6 as effort was concentrated on bird survey. The lone endemic frog, Platymantis minulus, is a Luzon endemic and usually restricted to forest habitats; this species was recorded only at Ipo CWA. Two resident frog species, Fejervarya cancrivora and Polypedates leucomystax, are common inhabitants of open areas and early secondary growth forest. Two invasive species, Rhinella marina and Kaloula pulchra, are strongly associated with human habitation and open areas. These two invasive species were present in Sites 1 and 5; it is highly likely that they are also present in other sites.

104. Anthropods. Above-ground sweeping and soil-litter sampling of arthropods within the project site resulted in a total of 642 individual arthropods representing 14 orders and 69 families recorded (Appendix 5.8). The most represented order (in terms of number of member families) were Coleoptera (beetles) and Diptera (flies) with 15 families each, Lepidoptera (butterflies and moths) and Orthoptera (grasshoppers) with six families, and Hymenoptera (ants, bees, and wasps) with five families. Much of the total abundance was attributed to only three orders, which accounted for more than 70% of the total number of recorded individuals. These were Hymenoptera with 218 individuals, Diptera with 180 individuals, and Lepidoptera with 73 individuals. Among the most dominant families were Formicidae (ants - O.Hymenoptera) with 211 individuals, Psychodidae (moth flies - O. Diptera) with 72 individuals, Sciaridae (fungus gnats - O. Diptera) with 69 individuals, and Nymphalidae (butterflies - O.Lepidoptera) with 35 individuals.

105. Species Conservation Significance. At least nine species present in the project area were chosen as noteworthy based on several characteristics: (1) restricted to Greater Luzon Biogeographic Region, (2) listed as globally threatened by IUCN, and (3) heavily exploited for food or taken as household pets. Five species of birds are noteworthy of which four are endemic to Luzon (already mentioned) whereas two species are classified as threatened species. The Luzon Tarictic and the Philippine Eagle Owl (Bubo philippensis) are classified as near-threatened and vulnerable, respectively. All of these noteworthy avian species were recorded at Ipo CWA and Isla Puting Bato.

106. Two species of mammals, the shrew rat Chrotomys sp. and the long-tailed Macaque (Macaca fascicularis) deserve special mention as the former is probably confined within Luzon (as most of its congeners are), and that the latter is heavily hunted either as food or as pets. The long-tailed Macaque is also listed in the CITES.

Page 54: Updated Initial Environmental Examination

40

107. Platymantis mimulus is known only from a very few localities on Luzon Island. It is a poorly known species, with information on ecology, reproduction, and population severely lacking. The monitor lizard Varanus marmoratus is heavily hunted across its known distribution.

4.2. The Air

4.2.1. Air Quality

108. Air quality and ambient noise levels in the study area were monitored from 30 July to 2 August 2013 (wet season) and 2-5 June 2014 (dry season).

109. There are no major sources of air pollution in the study area, which is largely given over to rural land uses. The ambient air quality sampled at Ipo dam site, San Mateo Barangay Hall and Bigte portal are within the DENR ambient air quality standards. The results are presented in Table 13.

Page 55: Updated Initial Environmental Examination

42

Table 13: Ambient Air Quality Results

Para eter Sa pli g ethod Test ethod

DENR sta dards

Reporti g li its

U its

AT - A

Near MWSS Bigte

property

- Jul

AT - A

Sa Mateo

Bara gay Hall Jul-

Aug

AT A

Ipo Da site - Aug

AT - A

Near MWSS Bigte

property

- Ju e

AT - A

Sa Mateo Bara gay

Hall - Ju e

AT A

Ipo Da site

- Ju e

Wet seaso Dry seaso

TSP Filt atio ethod y high-volu e sa ple

Fla e AAS . µg/N . . . . . .

SO

A so ptio i li uids fo gaseous polluta ts -

Ki oto B a d sa ple

Fla e AAS . µg/N . . . . . .

NO

A so ptio i li uids fo gaseous polluta ts -

Ki oto B a d sa ple

Fla e AAS . µg/N . . . . . .

PM Filt atio ethod y high-volu e sa ple

Fla e AAS µg/N . . . . .

P Filt atio ethod y high-volu e sa ple

Fla e AAS N/A . µg/N ND ND ND ND ND ND

CO Di e t ead out

a alyze Fla e AAS N/A . µg/N . . ND ND ND ND

42

Page 56: Updated Initial Environmental Examination

43

4.2.2. Noise Level

110. Main sources of noise in the study area arise from people, animals/insects (i.e. birds, dogs, crickets), vehicles, and wind. Noise level at the project site was measured using a digital sound level meter (precision type). Noise levels in Brgy. San Mateo and the Ipo dam site are all within the DENR limits and are typical of day-time noise levels in rural areas. There is a slight noise level exceedance observed in Bigte during the night-time (1900-2100). Results are presented in Tables 14 to 17.

Table 14: Noise Level Monitoring Results at MWSS Property Brgy. Bigte (Wet Season)

Sampling time / Date Class C (dB) DENR standard maximum

allowable noise level

Class C, dB

Remarks

1057-1257 / 30 July 2013 61.6 70 Passed

1257-1257 / 30 July 2013 61.1 70 Passed

1457-1657 / 30 July 2013 59.5 65 Passed

1657-1857 / 30 July 2013 55.3 65 Passed

1857-2057 / 30 July 2013 66.5 60 Exceeded

2057-2257 / 30 July 2013 52.5 60 Passed

2257- 0057 / 30-31 July 2013 52.3 60 Passed

0057-0257 / 31 July 2013 43.6 60 Passed

0257-0457 / 31 July 2013 42.5 65 Passed

0457-0657 / 31 July 2013 64.0 65 Passed

0657-0857 / 31 July 2013 62.6 70 Passed

0857-1057 / 31 July 2013 68.2 70 Passed

***Category “C”: A section primarily zoned or used as a light industrial area 0900H – 1800 H 70 dB (Daytime)[Maximum allowable limit based on division of 24-hour sampling] 1800H – 2200 H 60 dB (Evening)[Maximum allowable limit based on division of 24-hour sampling] 2200H – 0500 H 65 dB (Nigh time)[Maximum allowable limit based on division of 24-hour sampling] 0500H – 0900 H 60 dB (Morning)[Maximum allowable limit based on division of 24-hour sampling] Note: Monitoring was conducted on a 2-hour interval. In practice, the start of sampling time is used as the basis for noise divisions.

Page 57: Updated Initial Environmental Examination

44

Table 15: Noise Level Monitoring Results at MWSS Property Brgy. Bigte (Dry Season)

Sampling Date

Sampling Time

DENR standard maximum allowable noise level

Near MWSS Bigte

Property

100 m from the MWSS

Bigte

200 m from MWSS Bigte

500 m from MWSS Bigte

MWSS Bigte Portal

Salonga Property

Near Minuyan and Bigte Creek

Brgy Bigte Proper

Class C (dB) Class A (dB) Class C (dB) Class A (dB) Class A (dB) Class A (dB) 2- Jun – 14 10:00 – 12:00 70.00 55.00 62.50 63.30 66.00 65.80 2- Jun – 14 12:00 – 14:00 70.00 55.00 62.00 60.30 62.40 63.10 2- Jun – 14 14:00 – 16:00 70.00 55.00 57.90 52.50 61.60 64.20 2- Jun – 14 16:00 – 18:00 70.00 55.00 65.20 64.80 63.20 65.70

Average (daytime)

61.90 60.23 63.30 64.70

2- Jun – 14 18:00 – 20:00 65.00 50.00 55.90 54.60 56.60 63.30 2- Jun – 14 20:00 – 22:00 65.00 50.00 57.50 54.60 54.00 62.30

Average (evening)

56.70 54.60 54.00 62.30

2- Jun – 14 22:00 – 24:00 60.00 45.00 51.80 51.70 51.20 52.80 3- Jun – 14 00:00 – 02:00 60.00 45.00 43.00 46.60 42.60 57.20 3- Jun – 14 02:00 – 04:00 60.00 45.00 43.70 46.60 44.00 58.70 3- Jun – 14 04:00 – 06:00 60.00 45.00 46.30 43.00 46.80 57.98

Average (night)

46.20 46.98 46.15 57.98

3- Jun – 14 06:00 – 08:00 65.00 50.00 48.90 56.90 59.10 63.70 3- Jun – 14 08:00 – 10:00 65.00 50.00 56.00 58.20 60.50 64.60

Average (morning)

52.45 57.55 59.80 64.15

***Category “A”: A section which is primarily a residential area 0900H – 1800 H 65 dB (Daytime)[Maximum allowable limit based on division of 24-hour sampling] 1800H – 2200 H 60 dB (Evening)[Maximum allowable limit based on division of 24-hour sampling] 2200H – 0500 H 55 dB (nighttime)[Maximum allowable limit based on division of 24-hour sampling] 0500H – 0900 H 60 dB (Morning)[Maximum allowable limit based on division of 24-hour sampling] Note: Monitoring was conducted on a 2-hour interval. In practice, the start of sampling time is used as the basis for noise divisions.

***Category “C”: A section primarily zoned or used as a light industrial area 0900H – 1800 H 70 dB (Daytime)[Maximum allowable limit based on division of 24-hour sampling] 1800H – 2200 H 60 dB (Evening)[Maximum allowable limit based on division of 24-hour sampling] 2200H – 0500 H 65 dB (nighttime)[Maximum allowable limit based on division of 24-hour sampling] 0500H – 0900 H 60 dB (Morning)[Maximum allowable limit based on division of 24-hour sampling] Note: Monitoring was conducted on a 2-hour interval. In practice, the start of sampling time is used as the basis for noise divisions.

Page 58: Updated Initial Environmental Examination

45

Table 16: Noise Level Monitoring Results at Brgy. Hall San Mateo (Wet Season)

Sampling Time / Date Class C (dB) DENR Standard maximum allowable noise level Remarks

1250-1450 / 31 July 2013 66.8 70 Passed

1450-1650 / 31 July 2013 60.9 70 Passed

1650-1850 / 31 July 2013 64.2 65 Passed

1850-2050 / 31 July 2013 59.4 65 Passed

2050-2250 / 31 July 2013 61.4 60 Passed

2250-0050/ 31 July-1 Aug 2013 54.2 60 Passed

0050-0250 / 1 Aug 2013 47.5 60 Passed

0250-0450 / 1 Aug 2013 43.9 60 Passed

0450-0650 / 1 Aug 2013 51.6 65 Passed

0650-085 / 1 Aug 2013 64.0 65 Passed

0850-1050 / 1 Aug 2013 63.6 70 Passed

1050-1250 / 1 Aug 2013 62.2 70 Passed

***Category “C”: A section primarily zoned or used as a light industrial area 0900H – 1800 H 70 dB (Daytime)[Maximum allowable limit based on division of 24-hour sampling] 1800H – 2200 H 60 dB (Evening)[Maximum allowable limit based on division of 24-hour sampling] 2200H – 0500 H 65 dB (nighttime)[Maximum allowable limit based on division of 24-hour sampling] 0500H – 0900 H 60 dB (Morning)[Maximum allowable limit based on division of 24-hour sampling] Note: Monitoring was conducted on a 2-hour interval. In practice, the start of sampling time is used as the basis for noise divisions.

Table 17: Noise Level Monitoring Results at Brgy. Hall San Mateo (Dry Season)

Sampling Date Sampling Time

DENR standard maximum allowable

noise level San Mateo Barangay

Hall Remarks

Class C (dB) Class C (dB) 4- Jun – 14 15:30 – 17:30 70.00 63.00 Passed 4- Jun – 14 17:30 – 19:30 70.00 61.70 Passed 4- Jun – 14 19:30 – 21:30 65.00 62.40 Passed 4- Jun – 14 21:30 – 23:30 65.00 60.00 Passed

4- 5 Jun – 14 23:30 – 01:30 60.00 55.90 Passed 5- Jun – 14 01:30 – 03:30 60.00 46.20 Passed 5- Jun – 14 03:30 – 05:30 60.00 42.60 Passed 5- Jun – 14 05:30 – 07:30 65.00 56.50 Passed 5- Jun – 14 07:30 – 09:30 65.00 61.30 Passed 5- Jun – 14 09:30 – 11:30 70.00 64.70 Passed 5- Jun – 14 11:30 – 13:30 70.00 61.70 Passed 5- Jun – 14 13:30 – 15:30 70.00 61.80 Passed

***Category “C”: A section primarily zoned or used as a light industrial area 0900H – 1800 H 70 dB (Daytime)[Maximum allowable limit based on division of 24-hour sampling] 1800H – 2200 H 60 dB (Evening)[Maximum allowable limit based on division of 24-hour sampling] 2200H – 0500 H 65 dB (nighttime)[Maximum allowable limit based on division of 24-hour sampling] 0500H – 0900 H 60 dB (Morning)[Maximum allowable limit based on division of 24-hour sampling] Note: Monitoring was conducted on a 2-hour interval. In practice, the start of sampling time is used as the basis for noise divisions.

Page 59: Updated Initial Environmental Examination

46

4.3. Water

4.3.1. Climate

111. The project area climate falls under Type I climate of the modified coronas classification characterized as having two pronounced seasons, dry from November to April and wet during the rest of the year. Typhoons have greatly affected the climate and weather conditions in the area. An annual average of nine typhoons (1948-2004) made landfall or crossed the country, the majority of which hit Luzon Island where the project is located.

112. Climate trends were analysed by DOST PAGASA using available observed data from 1951 to 2009 with the average for 1971 as the reference value. Table 18 and 19 summarizes seasonal temperature and rainfall for the recent baseline (1971 to 2000) with future projections for Bulacan Province to 2065. At present, the temperature is equitable all-year round, with slightly higher temperatures in the dry season from March to May and prior to the main summer rains. The mean annual rainfall is about 2,385mm, with the maximum rainfall falling from June to August and least amount of rain observed from December to May. Future trends indicate an increase in mean monthly temperature of about 2°C by 2065, and an increase in annual rainfall to about 2,470mm with a seasonal shift to a more peaked rainfall distribution in the three summer months from June to August.

Table 18: Projected Temperature and Rainfall Change in Bulacan Province (Seasonal increase in temperature and rainfall)

Observed baseline Change in 2020 Change in 2050

Year 1971-2000 2006-2035 2036-2065

Months DJF MAM JJA SON DJF MAM JJA SON DJF MAM JJA SON

Seasonal increase in temperature

25.60 27.90 27.10 26.70 26.50 29.00 28.00 27.70 27.50 30.00 28.80 28.60

Seasonal rainfall change

212.40 288.90 1041.40 842.10 221.32 288.24 1042.73 841.86 184.36 183.74 1287.17 814.31

Table 19: Projected Temperature and Rainfall Change in Bulacan Province (Frequency on Extreme Events)

Provinces Stations No of Days w/ Tmax > 35°C No. of dry days No. of days with rainfall >200mm

OBS (1971-2000)

2020 2050 OBS (1971-2000)

2020 2050 OBS (1971-2000)

2020 2050

Frequency of extreme event

Manila Science garden

1095 1984 3126 7476 6302 6220 9 13 17

Source: Climate Change in the Philippines, February 2011, DOST-PAGASA

113. The study by DOST-PAGASA (Table 6b) predicted that the number of days with a maximum temperature greater than 35°C would almost double in the period 2006-2035 and triple in the period 2036-2065, compared with the baseline (1971-2000). The study also predicted that the number of dry days would decrease over the coming 50 years compared with the baseline with 7,476 days, falling to 6,302 between 2006 and 2035, and decreasing to 6,220 dry days in the period 2036-2065. There is also forecast to be a slight increase in the number of days with

Page 60: Updated Initial Environmental Examination

47

rainfall greater than 200mm from nine days for the baseline, to 13 days in 2006-2035, and 17 days in 2036-2065.

4.3.2. Seismology

114. Very little seismic data are available for the project area. The West Valley Fault (WVF) trace has been mapped fairly well and one study has been undertaken to establish seismic design parameters for the La Mesa dam, intake structures and spillway. However, only general results such as earthquake magnitude and peak ground acceleration (PGA) are available. In addition, available data suggest that the WVF trace runs roughly parallel to an average of 10km from the Angat Water Transmission Improvement System. It has been estimated that the WVF cangenerate a magnitude 7.2 to 7.4 event with a corresponding peak ground acceleration of approximately 0.67g.

Figure 13: Surface Water Quality and River Ecology Sampling Stations at Ipo Watershed

4.3.3. Hydrology and Surface Water Resources

115. The extensive area of the watershed results in a large volume run-off that is temporarily retained upstream of Angat dam although there are times when the water level rises to critical levels necessitating the release of extra run-off into the Angat river system. Releases from Angat dam, together with inflows from several small tributaries, flow into Ipo reservoir.

116. The low-lying embankment west of Brgy. Poblacion of Municipality of Norzagaray within the vicinity of Matictic Bridge is usually submerged under water if Angat dam releases water. During high volume rainfall, the areas on the western side of the river further downstream are also submerged from the run-off drained by Bayabas River that feeds into Angat River. These two areas are expected to be regularly inundated, and increasingly so in the future with the more intense rainfall events due to climate change. The rolling topography of the rest of the municipality with pockets of flat lands contributes to the concentration of extensive and regular flooding in these two areas.

Page 61: Updated Initial Environmental Examination

48

4.3.3.1. Surface Water Quality of the Angat Upper Reach

117. The Angat Upper Reach between Angat dam and Ipo dam is classified as Class B fresh surface water. This means that the river water quality is suitable for primary contact recreation such as bathing, swimming, and skin diving, particularly those designated for tourism purposes.

118. Water quality sampling and rapid site assessment were undertaken on 22 May 2013. Water samples were collected by grab sampling technique from eight sampling points from 5km upstream of Ipo dam to0.8km downstream. A suit of samples was collected from Angat River in the Municipality of Angat. The sampling points are shown in Table 20.

119. The in situ and laboratory results confirmed that the water quality is within the Class B standards for fresh surface water. Elevated fecal and total coliform are reported at the Ipo dam site and downstream of Ipo dam. These elevated measures can be attributed to settlements found near the dam site and downstream which is due to poor sanitation practices of the community.

120. Based on a one-year turbidity measurement made by CPF, it can be observed that the turbidity levels are high during the wet season.

Table 20: Surface Water Quality in Angat River (Upstream and Downstream of Ipo Dam)

Parameter, mg/L (unless stated)

Adopted Criteria

Reference IPO US2

IPO

US1 IPO4 IPO3 IPO2 IPO1

IPO

DS1

IPO

DS2

Angat River Downstream (Municipality of Angat)

Sampling date/ time

22 May 2013/ 14:48

22 May 2013/ 15:07

22 May 2013/ 15:24

22 May 2013/ 15:34

22 May 2013/ 15:47

22 May 2013/ 15:57

22 May 2013/ 16:46

22 May 2013/ 16:30

25 Aug 2013/ 15:35

Physical Characteristics

Temp (°C) Stabilizing parameter 28.88 29.73 30.20 28.60 29.90 29.48 31.95 31.63 25.80

Figure 14: Average Turbidity Level at Ipo Dam

Page 62: Updated Initial Environmental Examination

49

Parameter, mg/L (unless stated)

Adopted Criteria

Reference IPO US2

IPO

US1 IPO4 IPO3 IPO2 IPO1

IPO

DS1

IPO

DS2

Angat River Downstream (Municipality of Angat)

Sampling date/ time

22 May 2013/ 14:48

22 May 2013/ 15:07

22 May 2013/ 15:24

22 May 2013/ 15:34

22 May 2013/ 15:47

22 May 2013/ 15:57

22 May 2013/ 16:46

22 May 2013/ 16:30

25 Aug 2013/ 15:35

Salinity (%) Parameter not included in DAO90-34

4.55 10.44 9.98 9.47 9.82 9.83 9.78 9.76 14.10

Electric Cond. (µS/cm)

stabilizing parameter 7.00 6.00 4.00 9.00 11.00 8.00 8.00 5.00 220.30

Turbidity (NTU) 5 DAO 90-34 71.08 163.13 155.90 147.90 153.45 153.60 152.80 152.55 63.70

TDS 500 DAO 90-34 3.41 2.67 59.11 11.45 12.54 25.84 7.67 5.21 174.80

Inorganic and Non-metallic Constituents

pH 6.5 - 8.5 DAO 90-34 7.88 7.88 8.23 7.69 8.16 8.04 8.30 8.35 7.60

ORP (mV) 10 stabilizing parameter 188.25 227.25 174.63 200.50 200.25 213.50 98.38 211.00 211.00

Nitrogen (as NO3-)

Parameter not included in DAO90-34

<0.02 <0.02 <0.02 <0.02 <0.02 <0.02 0.02 <0.02

Phosphorus (as PO4

3-) 0.4 DAO 90-34 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006

Organic and Biological Constituents

BOD5 10 DAO 90-34 1.00 1.00 1.00 1.00 1.00 1.00 1.00 1.00

Dissolved Oxygen 6.5 – 8.5 DAO 90-34 8.90 8.15 8.89 8.52 8.43 8.69 8.75 6.25

Fecal Coliform (MPN/100mL) 200 DAO 90-34 22 36 181.50 66.00 245 150 81.50 210 3,500

Total Coliform (MPN/100mL) 1000 DAO 90-34 325.00 191.50 1,774.50 8,120.00 2,450.00 2,2210.00 1,260.00 4,870.00 5,400

Oil and Grease 2 DAO 90-34 0.40 0.40 0.70 0.40 0.60 0.70 0.60 0.50

Heavy Metals

Antimony (Sb) 0.005 DAO 90-34 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001

Arsenic (As) 0.01 DAO 90-34 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

Cadmium (Cd) 0.003 DAO 90-34 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006

Copper (Cu) 1 DAO 90-34 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02

Lead (Pb) 0.01 DAO 90-34 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

Mercury (Hg) 0.001 DAO 90-34 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001

Nickel (Ni) 0.075 WHO <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01

Vanadium (V) 0.075 WHO <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0

Zinc (Zn) 5 DAO 90-34 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02

Bromide 4.1 2 2.6 1.6 2.5 6.7 2.5 1.6 not measured

4.3.3.2. Surface Water Quality at Bigte and Sta. Maria River

Page 63: Updated Initial Environmental Examination

50

121. Surface water samples were collected from Bigte Creek during rainy season (August 2013). Samples were collected employing grab sampling technique from Bigte River, the creek near the MWSS property, and Sta. Maria River. Based on Class B surface water criteria, elevated measures were reported for turbidity, color, and total coliforms at all sites. Phosphorus and BOD are seen to have slightly elevated measures in Sta. Maria River.

Table 21: Surface Water Quality in Bigte River and Sta. Maria River

Parameter, mg/L

(Unless Stated) Adopted Criteria (Class B, )

SW2 SW03 SW Sta. Maria

Description Bigte river, sampling site is near the bridge

At Bigte, with the Salonga Property

Sta. Maria River

Physical Characteristics

Water use laundry, swimming, domestic

laundry, swimming, domestic

Temp (°C) 26-30 26.85 27.00 27.30

Salinity (%) 65 27.69 14.06 15.74

TSS 86 10.00 657.00

Electric Cond. (mS/cm) 432.7 219.70 246.00

Turbidity (NTU) 5 62.00 12.60 51.40

Colour (Apparent, PCU) 5 100 20.00 500.00

TDS 500 285.95 141.10 158.00

Inorganic and Nonmetallic Constituents

pH 6.5 - 8.5 7.65 8.33 8.20

ORP (mV) 201 211.00 187.00

Nitrogen (as NO ¯) 7 0.4 0.2 0.1

Phosphorus (as PO ³¯) 0.5 0.2 0.08 0.7

Organic and Biological Constituents

Dissolved Oxygen 5 13.40 22.5 not measured

BOD5 5 3 2 14

COD 9.9 9.8 49

Faecal Coliform (MPN/100mL) 100 24,000 9,200 920,000

Total Coliform (MPN/100mL) 1000 240,000 92,000 920,000

Oil and Grease 1 0.3 0.3 <0.3

Heavy Metals

Antimony (Sb) 0.005 <0.001 <0.001 <0.001

Page 64: Updated Initial Environmental Examination

51

Parameter, mg/L

(Unless Stated) Adopted Criteria (Class B, )

SW2 SW03 SW Sta. Maria

Description Bigte river, sampling site is near the bridge

At Bigte, with the Salonga Property

Sta. Maria River

Arsenic (As) 0.01 <0.01 <0.01 <0.01

Cadmium (Cd) 0.003 <0.006 <0.006 <0.006

Chromium (hexavalent, Cr(VI)) 0.01 <0.003 <0.003 <0.003

Copper (Cu) 0.02 <0.02 <0.02 <0.02

Lead (Pb) 0.01 <0.04 <0.04 <0.04

Manganese (Mn) 0.2 0.07 0.07 0.4

Mercury (Hg) 0.001 <0.0001 <0.0001 <0.0001

Nickel (Ni) 0.04 <0.01 <0.01 <0.01

Vanadium (V) 0.075 <1.0 <1.0 <1.0

Zinc (Zn)

2 <0.02 <0.02 0.1

Page 65: Updated Initial Environmental Examination

52

Figure 15: Surface Water and Groundwater Sampling Stations along Tunnel Segments

Page 66: Updated Initial Environmental Examination

53

4.3.4. Groundwater

122. Based on the Groundwater Availability Map of the Philippines, the project area is underlain by impermeable rocks with limited potential for groundwater resource. The geology varies from rocks without any known significant groundwater obtained through drilled wells to rock with limited potential to moderate permeability. Shallow water yields of less than 0.01L/s to 0.03L/s. Groundwater quality is soft to moderately hard.

123. The information on groundwater use in the project area is very limited. Communities are getting their drinking water supply from the local water district (LWUA, Local Water Utilities Administration) and distributed by water trucks or shallow wells.

124. Groundwater wells registered at the National Water Resources Board (NWRB) include two Norzagaray water district wells in Brgys. Partida and Matictic in the Municipality of Norzagaray, Province of Bulacan with 31.95m and 8.11m pumping water level, respectively.

125. Data on groundwater levels were also obtained from 10 boreholes drilled within the project area. The 2013 borehole report shows that the water table is found in Segment 4 at about 4.5mbg; Segment 6 at about 15.5mbg and Segment 7 at 9.5mbg.

Table 22: 2013 Borehole and Water Table

Borehole no. Location

Elevation (masl)

Depth as drilled meters

Depth to water table

Remarks

BH-1 River hole. Bedrock not reached (Segment 1) 82.469 16 - River hole; no

measurement of water

BH-1A River hole. Bedrock reached (Segment 1) 25.5 - River hole; no

measurement of water

BH-2 Intake Area (Tunnel) (Segment 1) 98.969 Not drilled Not drilled -

BH-3 Tunnel (Segment 1) 142.015 25 15.10 -

BH-4 Tunnel (Segment 4) 248.156 45 4.5 -

BH-4A Tunnel (Segment 6) 40 15.5 -

BH-5 Upstream, Tunnel Outlet Portal (Segment 7) 122.746 30 - Hole dry

BH-6 Tunnel Outlet Portal (Segment 7) 97.189 20 8.45 -

BH-7 Connecting Channel (Segment 7) 96.139 16.5 - Hole dry

BH-8 Connecting Channel (Segment 7) 97.849 12 9.5

*Chromium (total) maximum value. No value on hexavalent chromium

4.3.5. Freshwater Ecology

126. Sampling sites of the freshwater ecology cover two general areas that are perceived to be the ‘impact’ areas of the proposed project: (a) within the vicinity of Ipo dam where the intake channel would be located and (b) within the vicinity of Bigte river where the exit tunnel construction would be located. In each of these sites a 50m stream length was designated as the sampling area. These sampling sites are presented in Table 25.

Page 67: Updated Initial Environmental Examination

54

Table 23: River Ecology Sampling Stations

May 2014 Sampling

August 2013

Sampling General Remarks

Site 1 1po Lake upstream (1L-US)

Site 1. Ipo Dam upstream

IPO US2 8/23/2013; 1050h; sampling after storm Maring; cloudy; with few hours of sunlight in the morning but with light to heavy rains in the late afternoon and evening. Sampling about 100m from the Angat spillway; depth about 3m; molluscan fauna are lesser in number; stone and rocks with few insects; 50m downstream with stony muddy substrate; reported by fishermen - tilapia, carp, kanduli, biya, halfbeaks, gourami. 5/22/2014; sampling about 100m from the Angat spillway; depth about 3m; predominantly stony/rocky lake banks and 50meters downstream with stony muddy substrate.

Site 2 Ipo Lake midstream (IL-MS)

Site 2. 1po Dam midstream

IPO US1 8/23/2013; banks with generally good vegetation cover but with one area observed to be recently eroded; with human habitation in relatively flat areas. 5/22/2014; banks with generally good vegetation cover but with one eroded area seen in August 2013 still is eroded; with human habitation in relatively flat areas.

Site 3 Ipo Lake SapangMunti (IL-SM)

IPO 4 5/22/2014; relatively shallow, some areas with submerged grass vegetation; sandy muddy substrate.

Site 4 Ipo Lake Dam Site(IL-D)

Site 3. Ipo Dam site

IPO 1,2,3 8/23/2013; banks with infrastructure generally with good vegetation cover; proposed tunnel inlet site, 5/22/2014; banks with infrastructure generally with good vegetation cover; proposed tunnel inlet site

Page 68: Updated Initial Environmental Examination

55

May 2014 Sampling

August 2013

Sampling General Remarks

Site 5 Angat river below Ipo Dam Site (AR-D)

Site 4. Angat below Ipo Dam

IPO DS1 8/23/2013; substratum stony-rocky with boulders; water murky; with about 50m. 5/22/2014; substratum stony-rocky with boulders; water greenish; with about 50m; human habitation with a number of domestic animals; fish sampling was done in 5/23/2014.

Site 6 Angat 1km down-stream of Site 4 (AR-DS)

IPO DS2 5/22/2014; substratum stony-rocky with boulders; water murky; with about 50m; fish sampling was done in 5/23/2014

Site 7 Angat River at Bitbit Bridge (AR-BB)

IPO DS5 5/23/2014;substratum stony-rocky with boulders; water clear; shallow; within a river resort establishment

Site 8 Angat at Sta Cruz, Angat (AR-A)

Site 7. Angat River at Angat

Angat 8/23/2013;main channel of Angat River in Angat town 5/23/2014; main channel of Angat River in Sta. Cruz, Angat town; urban area in one bank and agricultural land in the other; multi-purpose domestic use observed.

Site 9 Bigte tributary along Manila Water Bldg (BR-MW)

Site 5. Bigte River tributary

SW BIGTE 1 8/23/2013;Small stream in the old seedling site of MWSS; stream joins Bigte River about 15m downstream; gravel-sand-mud substrate; proposed tunnel outlet site. 5/23/2014; small stream in the old seedling site of MWSS; stream joins Bigte River about 15m downstream; gravel-sand-mud substrate; proposed tunnel outlet site.

Site 10 Bigte River under Bigte Bridge (BR-BB)

AT4 SW2 5/23/2014; perceptively influenced by domestic and commercial waste; water dark and smelly; substratum of cement slabs for most part.

Site 11 Sta Maria under San Jose bridge (SM-S1)

Site 6. San Jose River bridge

STA MARIA 8/23/2013; Sta. Maria River underneath the bridge in San Jose del Monte in Bulacan; Bigte River is a tributary of this channel. 5/23/2014; San Jose River underneath the Sta. Maria Bridge in Bigte; just after Bigte River joins it.

Site 12 Sta Maria Townsville (SM-TV)

TOWNVILLE 5/23/2014; San Jose River in Townsville; about 1km upstream of Site 11.

Page 69: Updated Initial Environmental Examination

56

104. In all sites, the phytoplankton is predominant to the zooplankton. There were 21 phytoplankton genera collected and identified compared to five zooplankton taxa. Plankton thrive best in relatively still waters; thus, the lake sites have relatively higher indices.

105. No insect larva was collected in the suitable environments. Macrobenthic insects usually prefer a hard substratum. The conditions in the dam sites do not generally satisfy this requirement. With the large quantity and the turbidity of water, this becomes a stressful environment for aquatic macro-benthic insects. In the river sites, the increase flow and volume of water can easily displace these organisms from their habitat.

106. Collected molluscs are typical and comparable to those found all over the Philippines. Of the molluscan species collected, Brotia asperata and Corbicula manilensis are also collected for table consumption by the locals.

107. The shrimp and crab fauna are still relatively species poor with only four genera present, Macrobrachium, Atyopsis, Caridina, and Varuna. Almost all taxa were present in the sites where fish sampling was also done. The catch is small, just about 100g.

108. Seventeen species of fishes were collected from the sites. More species were collected in the lake waters, with the predominance of tilapia and ayungin in the catch. Because of the unfavourable weather conditions, a less than systematic sampling could only be done.

4.4. People

4.4.1. Population and Communities

109. The Municipality of Norzagaray, where the water transmission line (Tunnel 4) will be constructed, is in the southeast of Bulacan bordering the Municipality of Montalban, Rizal Province. It is bound on the north by the Municipality of Doña Remedios Trinidad, by the Municipalities of Angat and Sta. Maria in the west and by the City of San Jose del Monte in the southwest. It is part of the third congressional District of Bulacan together with Angat, San Rafael, San Ildefonso and San Miguel, all on the eastern side of Bulacan.

110. More than one-third of the municipality ‘s land area is within Angat watershed that was delineated through Proclamation 71 dated 10 March 1927 covering a total area of some 62,310ha of the Sierra Madre Mountain Range in the Province of Bulacan and Nueva Ecija. The Angat and Ipo dams are located in the watershed boundary. The dams are notable for being a major water and power supply for Metro Manila.

111. Norzagaray belongs to the third district of Bulacan and is classified as 1st class municipality. It has a total land area of about 288.52km² (Table 24).

Page 70: Updated Initial Environmental Examination

57

Table 24: Municipal Profile of Norzagaray, Bulacan

Founded 1857

Total of barangays 13

Total area 288.52km²

Population 2010 103,095

Density 360 km²

District 3rd District

Income class 1st Class

Regional classification Region 3

112. At present, Norzagaray is divided into 13 barangays with an estimated total land area of some 30,819ha, excluding some 1,607ha contested with Doña Remedios Trinidad and San Jose del Monte. Brgy. San Mateo is the second largest in terms of land area representing 24.13% while Bigte is the 9th largest representing 1.89% of the total municipal land area.

Table 25: Population/Growth Rate of Norzagaray, Bulacan

Year Population ±% p.a

1995 2000 2007 2010

51,015 76,978 105,470 103,095

- 8.58 4.60 -0.76

113. Between 1995 and 2007, the municipal population was more than double. This was the result of

the relocation programs of the national government, the populations of Brgys. Tigbe and Bitungol increased rapidly between 1995 and2000 primarily due to migration toward the resettlement sites of North Village Housing (NVH) and Friendship Village Resources (FVR). On average, 2,226 persons annually relocated into Norzagaray between 2000 and 2007. This caused undue burden for the local government unit (LGU) to provide for the increase demand for social services and facilities.

114. Norzagaray is a net in-migration area from 2000 to 2007 (NCSO/Municipal Civil Registrar Office). In 2010, however, population slightly decreased due to out-migration. There are significant number of laborers and unskilled workers among the employed persons, followed by trade and related workers, plant and machine operators and assemblers, farmers, forestry workers and fishermen. With the increase of the construction activities in the area due to Tunnel 4 construction, including the increased requirement of the cement factories and their respective quarry sites, the inadequacy of livelihood and employment opportunities were given a boost and this included the resettled families in the area. Skills training, capability building and financial assistance were provided to the new settlers and several women were trained in rag-making

Page 71: Updated Initial Environmental Examination

58

which grew into a livelihood opportunity for the residents.

115. Norzagaray, being a first class municipality, generates more than half of its revenue from local business locators, quarrying and cement manufacturing, including hydropower plant and other industries. Less than 40% come from Internal Revenue Allotment (IRA) from the national government.

4.4.2. Health Facilities

116. Primary health services are provided to Norzagaray residents through a network of a municipal hospital and two rural health units. This is complemented by six privately operated health facilities. The Norzagaray Municipal Hospital is located in Brgy. Poblacion and is being operated by the municipal government and also caters for the primary health care needs of neighbouring municipalities. In terms of water access, only 66.45% have access to safe water in Bigte and 28.45 % in San Mateo. The Bulacan Bulk Water project is currently being planned by the MWSS and Manila Water to supply the needs of the municipalities of the Province of Bulacan.

4.4.3. Education Facilities

117. The municipality provides the basic primary high school and a municipal college for its constituents. Pre-school and day-care and kindergarten are operated in each barangay of the municipality.

4.4.4. Socio-economic Conditions

118. The local economy is dominated by the service sector, followed by industry, and then the agriculture, fishery and forestry sector. Table 26 shows the distribution of employment by sector.

Table 26: Sectoral Distribution of Employment CY 2000, Bulacan and Norzagaray

Sector Bulacan Norzagaray

Municipality (%) Prov Sector (%)

Agricultural, Fishery, and Forestry

12.40 12.43 3.27

Industry 27.26 29.21 3.50

Services 60.34 58.36 3.16

Total 100.00 100.00 3.27

Source: CLUP Norzagaray/National Statistics Office (NSO)

119. The contribution of the mining sub-sector in the industry is significant and slightly higher in Norzagaray than the province. However, it may be seen that the total employment share of Norzagaray is a mere 3.27% of the province. The high location quotient is due to the accessibility of the quarry areas and establishments of the three large cement manufacturing plants (Republic cement, Holcim and La Farge) contribute to this comparative advantage. In addition, it has also exhibited and continues to exhibit an advantage compared to the other municipalities of Bulacan in electricity, gas and water, construction and wholesale and retail trade. This is due to the continuing operation of NPC’s Angat Dam Hydro Electric Power Plant, the Trans Asia Power Generation Corporation and the MWSS Ipo Dam.

120. Data from the Municipal Agricultural Office show that as of December 2007, the municipality has an estimated 9,250ha of agricultural lands but more than half of the of this is not used for crop

Page 72: Updated Initial Environmental Examination

59

production and remains covered with grass. Of the municipality’s agricultural lands, only around 44% are used for production activities. Almost a third (3,278ha) is used for crop production while some 780ha are used for livestock and fishery production. Rice, mango, banana, and root crops are the mostly extensively grown crops. But only 14% of the rice lands are irrigated. In some areas, rice lands have remained untilled or abandoned as prospective expansion areas of the existing quarry operations.

Table 27: Extent and Average Yields of Agriculture Land Use: Norzagaray

Crops/Livestock Area (Has) (%) No. of Farmers Ave. yield / mt / ha / year

Crops 3,287.43 35.51 4,379

Rice - Rainfed 1,152 12.44 1,o56 4.17 - Irrigated 162 1.75 268 3.77

Mango 665.71 7.19 885 5.37 Banana 429.82 4.64 575 4.19

Coconut 142.04 1.53 630 11.34 Coffee 21.15 0.23 55 0.16 Root Crops 228.71 2.47 322 9.27 Other crops 486 5.25 853 4.6 Livestock 780.52 8.43 2,900

Swine 20.9 0.23 602 7.05 Large Cattle 303.1 3.27 1,366 7.05 Native Chicken

0.87 0.01 605 4.32

Broiler 4.37 0.05 167 4.32 Fishery 450.92 4.87 160 0.59 Grassland 5,190.05 56.06 0 Total 9,258.00 100 7,279

Source: CLUP Norzagaray/ 2007 Municipal Agricultural Profile

121. In addition to cement production, Norzagaray hosts companies that manufacture feeds (Subjin), roofing materials (Vasquez), agrochemicals (Oria), fireworks (Nomilyn and DSP), and corrugated carton (Jennson), among others.

4.4.5. Physical Cultural Resources

122. The only physical cultural resource (PCR) near the MWSS tunnel ROW is Pinagrealan Cave. The Pinagrealan Cave near the Bigte segment and is about 450m away from the tunnel ROW. It is a declared historical landmark by the National Historical Commission of the Philippines. The local government of Norzagaray also recognizes its historical and tourism importance. The application of the cave as protected area under NIPAS is ongoing.

4.4.6. Historical Background and Unexploded Ordnance (UXO)

123. The project site has been a guerrilla site during the Japanese – American war in 1942-45. The following figure shows the guerrilla sites in Luzon.

Page 73: Updated Initial Environmental Examination

60

Figure 16. Guerrilla site map and project site

124. The site has a probability of UXO being present on site. Identification and disposal of UXO of critical importance prior to commencement of any construction work to ensure safe working environment is provided.

4.4.7. Indigenous People

125. Indigenous peoples (IP), known as Dumagats, reside in the mountains of Norzagaray, particularly in San Mateo and San Lorenzo. About 367 IPs live in San Mateo while 8 IPs live in Bigte.

126. Currently, CADT application of the Dumagats of Brgy. Kabayunan, Municipality of Dona Remedios Trinidad Bulacan, Brgys. San Lorenzo, San Mateo and San Isidro, all in the municipality of Norzagaray Bulacan is being processed by the NCIP regional office. Social preparation activities were already undertaken as of November 2013 and delineation of the claimed ancestral domain is being prepared. A total of 593 families are claiming CADT ownership. About 209 families from Sitio Ipo, 13 families from Sitio Paco , 48 families from Sitio Anginan/Santol and 53 families from Sapang Munti, all from Brgy. San Mateo, Norzagaray Bulacan are included as CADT claimants.

127. The Karahume Ancestral Domain Sustainable Development and Protection Plan (ADSDPP) was completed in December 2008 and endorsed by the Sangguniang Bayan of Norzagaray on 20 July 2009. The ADSDPP of Karahume envisions, “to have a peaceful, progressive, environment friendly and self-sustaining Dumagat community wherein human rights is respected by the state and the rights for better education, good health, better livelihood programs are guaranteed by government.”

128. The ADSDPP implementation, covering about 1,145ha targeted as mix land use, faces crucial challenges due to multiplicity of land tenure instruments over portions of the CADT, of which portions of the CADT fall within the proclaimed forest reserves of the MWSS and NPC (Presidential Proclamation Nos. 391 and 599 and a CBFM issued by DENR).The mixed land use

AWTIP

Project Site

Page 74: Updated Initial Environmental Examination

61

includes (i) agricultural (351ha), (ii) cemetery (2ha), (iii) communal forest (303ha), (iv) eco-tourism (7ha), (v) pasture land (59ha), (vi) reforestation (782ha), (vii) residential (81ha), and (viii) sanctuary (232ha). The other issues include the intrusion of the non-IPs upland farmers and trading of land rights over portions of CADT.

129. At present, in addition to the Karahume CADT, the Dumagats have applied CADT for the entire Angat Watershed and Forest Reserve, including the portion of the project site – Segment 1.

4.5. Summary Description of the Project Segments

130. Segment 1 (Ipo dam site) is a forest zone. It is also in a build-up zone of the Ipo watershed-controlled zone. It is a part of a protected area, the Angat Watershed Forest Reserve (55,000ha managed by NPC), Angat Watershed and Forest Range (Pilot)/Ipo Watershed managed by DENR and MWSS. There are no physical cultural resources found in this segment. About 49 structures were found at 60m ROW. The depth of the tunnel is about 100m to 200m in the basalt rock formation at this segment. The segment is covered with tree-dominated vegetation, mostly domestic trees but has low diversity. No endemic vegetation species was found. There is a moderate diversity in wildlife. Groundwater quality must be within DENR standards. Results in surface water have shown that coliform counts were reported at the confluence of Sapang Munti and Ipo and downstream of the dam past the community site. The air quality should also be within DENR standards. The CWA for the construction of the inlet structure will be located at Segment 1 which is about 1ha. The CWA includes material storage, workers’ cam. An existing dirt road down the hill and finally to the intake structure site can be used during the construction phase.

131. Segment 2 (San Mateo Rolling Terrain) is located in a residential zone, forest zone and forest buffer zone. It is found within the indicative boundary of Angat Watershed Forest Reserve. A total of 18 infrastructures were found within the 60m ROW. The tunnel will traverse basalt and sediment rock formation at about 125mbg to 200mbg. Segment 2 vegetation was dominated by brushland. No endemic vegetation species was found. This segment has low to very low vegetation diversity and low wildlife diversity. No endemic wildlife species was found. The groundwater and surface water qualities must be within the DENR standards and air quality.

132. Segment 3 (AFP housing) is located in a forest buffer zone. It was not a part of protected area and no physical cultural resources were found on this segment. A total of 201 infrastructures, mostly housing units of the AFP subdivision, were identified within the 60m ROW. The tunnel traverse’s sediment and volcanic rock formation at about 100mbg to 125 mbg. This segment is covered by residential, subdivisions, cultivated area and brushland. It has low to very low vegetation diversity and low wildlife diversity. No endemic wildlife species were found. Groundwater and surface water qualities must be within the DENR standards and air quality.

133. Segment 4 (Grassland) is located in a forest and residential buffer zones. The barangay cemetery is located 300m away from the tunnel ROW. A total ofeight infrastructures were found within the 60m ROW. The tunnel traverses Alagao volcanic rock formation at a depth of about 100m to 125 m. The vegetation in this segment comprises of grassland and brushland. This segment has low to very low vegetation diversity and low wildlife diversity. No endemic wildlife species was found. Groundwater and surface water qualities must be within DENR standards and air quality.

Page 75: Updated Initial Environmental Examination

62

Figure 17: Project Segments

Page 76: Updated Initial Environmental Examination

63

Figure 18: Location of the Inlet and Associated Works

134. Segment 5 (Road ROW) is located in residential and agricultural zones. It is not a part of a protected area. No physical cultural resources were found near this segment. A total of 13 infrastructures were found within the 60m ROW. The tunnel depth is about 100m to 125m and traverses Alagao volcanic rock formation. Segment 5 vegetation comprises of grassland and brushland. This segment has low to very low vegetation diversity and low wildlife diversity. Groundwater and surface water qualities must be within DENR standards and air quality.

135. Segment 6 (Grassland) is located in a residential and agricultural zone. It is not a part of a protected area. No physical cultural resources identified near this segment. A total of12 infrastructures are within the 60m ROW. The tunnel depth is about 50m to 100 m and traverses Alagao volcanic rock formation. This segment is dominated with grassland and brushland. This segment has low to very low vegetation diversity and low wildlife diversity. No endemic wildlife species were found. Groundwater and surface water qualities must be within DENR standards. The elevated noise level is observed at 19:00 to 21:01.

136. Segment 7 (Brgy. Bigte) is located in residential, agricultural zone and quarry zone. Pinagrealan Cave is about 450m away from tunnel ROW. It is considered tourist attraction and historical landmark in Norzagaray. There are about 23 infrastructure found within the 60m ROW. The tunnel depth is about 20mbg to 50 mbg and traverses volcanic and limestone rock formation. This is the outlet location and the area is dominated by rain tree and mahogany while the proposed disposal area is dominated by open-type vegetation. This segment has low to very low vegetation diversity. Endemic species found is narra (Pterocarpus indicus). There is moderate wildlife diversity in this segment. Groundwater quality must be within DENR standards, while results in surface water have shown a high coliform measure. Elevated noise level is observed at night-time between 19:00 to 21:00.

TEMPORARY SPOIL

DISPOSAL AREA

CONTRACTOR’S WORKERS’ AREA

Page 77: Updated Initial Environmental Examination

64

Figure 19: Location of the Outlet Structure

V. Potential Impacts and Mitigation Measures

137. The key potential impacts caused by the construction of Tunnel 4 using TBM tunnelling method

is presented below.

5.1. The Land

138. Potential impacts on land during the construction phase includes soil and erosion; loss of vegetation; disturbance to wildlife; generation of spoil, solid waste and hazardous waste.

Table 28: Potential Impacts on Land

Potential Impact Options for prevention or mitigation or enhancement CONSTRUCTION PHASE

Soil and Erosion due to:

(a) soil disturbance (b) vegetation clearing

Location: Inlet structure and relevant work sites

(a) Confine soil disturbance and/or vegetation clearing to pre-defined and planned area that includes project footprint and needed easements

CONTRACTORS’ WORK AREA

TEMPORARY SPOIL

DISPOSAL AREA

Page 78: Updated Initial Environmental Examination

65

Potential Impact Options for prevention or mitigation or enhancement (b) Stabilize exposed soils with temporary seeding,

mulches, mats, non-chemical-based soil binders. (c) Protect slopes with any one or combination of

bonded fiber matrices, erosion control blankets, silt fence, fiber rolls, and keeping stormwater off the slopes through diversion channels and/or berms.

(d) Re-vegetate disturbed soils/slopes as soon as possible after completion of the construction works.

(e) Replacing vegetation that died during the defects liability period.

At the active work sites,

Provide temporary drainage with sedimentation tank or filters such as block and gravel, prior to discharge to watercourses

Loss of vegetation due to:

(a) vegetation clearing and potential trampling of trucks/equipment beyond project footprints

(a) Institute measures to avoid impacting on habitats and wildlife, such as: (i) minimize vegetation clearance at the intake and

outlet (ii) fence off vegetation to be retained (iii) provide environmental training for workforce (iv) enforce site rules and sanctions to discourage

workforce from hunting, fishing and poaching. (b) Confine all construction activities to previously

disturbed areas, to the extent practicable, e.g., workers’ quarters/camps.

(c) Use existing roads for project activities. Minimize new road construction.

(d) To avoid unnecessary clearing, mark/delineate areas to be cleared of vegetation, e.g. by fencing.

(e) Re-vegetate construction sites using local, indigenous species.

(f) Limit any collection of wood for charcoal to exotic i.e. non-native species.

Performance Indicator

Minimal number of trees applied for tree cutting permit from DENR

Disturbance to wildlife due to

(a) Construction noise, vibration, dust, lighting, presence/movement of people, etc.

(a) Implement measures to mitigate noise, vibration and dust.

(b) Strategically place nets at the tunnel portals to prevent flying debris.

(c) Water to minimize dust accumulation and spreading.

Performance Indicator

Record of number of poaching and illegal trading of wildlife by workers

Page 79: Updated Initial Environmental Examination

66

Potential Impact Options for prevention or mitigation or enhancement

Generation of spoil and spoil disposal.

More than 150,000m3 is expected to be generated due to tunnelling works, which is about 190,000 m3 loose volume.

(a) Prepare and implement a plan for the preparation of the spoil disposal areas.

(b) Minimize the volume of spoil to be disposed of by re-use in backfilling of roads, and by offering as free filling materials to government projects needing backfill materials.

(c) Disposal area must be confined to solid ground, of low ecological and agricultural value.

(d) Disposal area must not occupy drainage lines and streams and create an obstacle to streams or induced flooding.

(e) Spoil heaps must be designed and shaped with stable side slopes and suitable drainage.

(f) Spoils heaps must be compacted during the earthworks.

(g) On complete, the spoil heaps must be covered with the original top soil from the site and re-vegetated

Solid waste (a) Implement an eco-friendly solid waste management at work sites and workers’ camp/s, which minimizes, re-uses, segregates and promptly disposes of generated solid waste.

Hazardous waste

(a) Locate stationary ground storage for hazardous waste at least 100 m away from water bodies, raised to min 1 ft above high flood level. Or, use mobile storage but should not be parked near water bodies.

(b) Secure storage areas appropriately. Storage facilities must be able to contain spillage.

(c) Dispose of waste promptly and appropriately. (d) The contractor shall be required to implement an

appropriate hazardous waste management program.

(e) Storage of oil and grease, other chemical and additives used for the maintenance and operation of heavy equipment shall be properly built and maintained, to include bunded storage for the capacity of the containers plus 10%, and oil traps on drainage outfalls.

(f) Chemicals such as injection resin, micro fine cement, ready mix shotcrete and admixture will be used in the construction of Tunnel 4. The cured products are harmless. However, if cured prior to application and hardened, it will become an inert material just like the excavated materials. Such materials should be transported and disposed of the same as the spoil.

Page 80: Updated Initial Environmental Examination

67

5.2. Air 139. Potential impacts on air during the construction phase includes Deterioration of ambient air

quality; and high level of noise.

Table 29: Potential Impacts on Air

Potential Impact Options for prevention or mitigation or enhancement

CONSTRUCTION PHASE

a) Deterioration of ambient air quality especially in areas located near the tunnel outlet due to dust, concrete dust and gas emissions from:

(i) Earthworks and other

construction processes; tunnelling (TBM);

(ii) stockpiling of aggregates and spoils, and conveyance of spoils to disposal areas;

(iii) increased transport activities in the construction areas and along Ipo Road;

(iv) burning of vegetation and wastes; and

(v) operation of mechanical equipment

(vi) spillage of uncured cement additives

At the project area, locate emission sources away from sensitive receptors, e.g., concrete batching and rock crushing plants at least 500m upwind of sensitive receptors.

In active work sites:

(a) Apply dust suppression techniques, e.g., watering with bowsers, sheeting particularly at Bigte area

(b) Water dry unpaved/exposed surfaces, stockpiles of sand and excavated materials, at least twice daily, or as necessary.

(c) Protect aggregate stockpiles with sheeting to restrict the movement of dust.

(d) Require trucks, particularly those hauling aggregates, to have secure covers.

(e) Limit engine idling to 5 minutes.

Prohibit open burning of vegetation and other waste in the project area

Ipo Road, main access road, other roads in the Project area,

Limit speed of all construction vehicles to maximum of 40 kph on the access road to, and max. 30 kph in, the site.

Performance Indicator

Maintain air quality within national air quality standards, or if these are not available, internationally accepted air quality standards, such as WHO Air Quality Guidelines Global Update, 2005

Page 81: Updated Initial Environmental Examination

68

Potential Impact Options for prevention or mitigation or enhancement

Parameter Averaging Period Guide µg/m3

SO2 24 hrs 20 NO2 1 year

1 hour 40 200

PM10 1 year 24 hrs

20 50

PM2.5 1 year 24 hrs

10 25

Noise and vibration in the project area where TBM tunnelling will commence, vehicle and equipment operations

(a) Use only equipment that emit least noise and vibration and are well maintained.

(b) Use facility layout to minimize noise propagation e.g. using topography / existing buildings as barriers, where possible locate noisy activities away from local communities.

(c) Control noise at source, e.g. low noise plant, muffling, acoustic screening, switch off campaigns.

(d) Restrict use of noisy and highly vibrating equipment from 8AM-5PM. Necessary overtime work should: a) not go beyond 9:00PM; b) observe regulated noise and vibration levels; c) not use noisy and highly vibrating equipment; and d) should be coordinated with the barangay and affected households.

(e) Manage the ins and outs of hauling trucks. Spread out the schedule of material, waste and spoil transport in the day (off-peak hours).

(f) Enforce the rule of no blowing of horns. (g) Strictly enforce upon workers the compliance with

wearing of ear mufflers, especially those who are operating equipment.

Performance Indicator

Adopt national standards for construction sites and residential areas if available.

***Category “A”: A section which is primarily a residential area

Page 82: Updated Initial Environmental Examination

69

Potential Impact Options for prevention or mitigation or enhancement

Time Sound level limit, dB

0900H – 1800

H

(Daytime)[Maximum allowable

limit based on division of 24-

hour sampling]

65

1800 H – 2200 H (Evening)[Maximum allowable

limit based on division of 24-

hour sampling]

60

2200 H –

0500 H

(NIghtime)[Maximum

allowable limit based on

division of 24-hour sampling]

55

0500H – 0900

H

(Morning)[Maximum allowable

limit based on division of 24-

hour sampling]

60

Note: Monitoring was conducted on a 2-hour interval. In practice, the start of sampling time is used as the basis for noise divisions.

***Category “C”: A section primarily zoned or used as a light industrial area

Time Sound level limit, dB

0900H – 1800

H

(Daytime)[Maximum allowable

limit based on division of 24-

hour sampling]

70

1800 H – 2200 H (Evening)[Maximum allowable

limit based on division of 24-

hour sampling]

60

2200 H –

0500 H

(NIghtime)[Maximum allowable

limit based on division of 24-

hour sampling]

65

0500H – 0900 H (Morning)[Maximum allowable

limit based on division of 24-

hour sampling]

60

Note: Monitoring was conducted on a 2-hour interval. In practice, the start of sampling time is used as the basis for noise divisions.

Alternatively use internationally accepted standards such as WHO. Reference / jurisdiction

Ambient standard

Guidelines for Community Noise, WHO, 1999 International

Receptor: Residential; institutional; educational Daytime (07:00-22:00): 55dBA Nighttime (22:00-07:00): 45dBA Receptor: Industrial; commercial 70dBA throughout the day

5.3. Water

140. Preliminary construction works such as clearing can generate lose ground materials that in a heavy rain are mobilized potentially including uncured fine cement, admix causing siltation to Bigte Creek and Angat River. This may result in the reduction of light penetration limiting growth of organism in water bodies; and high turbidity level of water transmitted to Maynilad Treatment

Page 83: Updated Initial Environmental Examination

70

Plants in Quezon City.

141. During the actual construction of tunnel and other associated structures/ facilities, more areas will be cleared in the increasing the volume of easily erodible loose earth materials. This may result to loading of organic materials in the Bigte Creek and Angat River and may subsequently result to eutrophication which is detrimental to water bodies.

142. The project is expected to discharge effluents in water bodies. There will be quarterly monitoring of water quality and semi-annual monitoring of freshwater ecology primarily during the construction phase which will provide meaningful ecological information to analyse the impacts of tunnel construction and operation on the river ecology of Angat River and Bigte Creek and public health of population living in the vicinity of these water bodies.

Table 30: Potential Impacts on Water

Potential Impact Options for prevention or mitigation or enhancement

CONSTRUCTION PHASE

Impact on surface water quality due to/ from:

(a) Contaminants from materials used and construction activities and processes

(b) Siltation from soil erosion, spoil disposal area, dewatering excavations, water discharge from water treatment plant etc

At the active work sites

Mitigating contaminants

(a) Provide adequate water supply, sanitation facilities at work sites and workers’ camp. A water treatment facility will be installed in Bigte work site. Enforce observance of good sanitation practices by workers.

(b) Chemicals such as injection resin, micro fine cement, ready mix shotcrete and admixture will be used during construction. The cured products are harmless. Uncured products should be prevented from entering the water bodies. Spillage must be collected using absorbent materials such as sawdust and sand and dispose of in accordance with local regulations.

(c) Implement solid waste management that minimizes, re-uses, properly segregates and promptly and properly disposes of generated solid wastes.

(d) A coffer dam during the construction of inlet and outlet and/ or drainage system should be properly constructed in the inlet and outlet areas to minimize siltation especially during heavy rain. If possible and necessary, it should be supplemented with commercially available, silt curtains, geotextiles or coconets/cocologs. Silts that accumulate should be removed regularly and disposed of properly or buried and overlain with vegetation to minimize further mobilization.

(e) Implement hazardous waste management that minimizes, properly segregates and promptly and properly disposes of generated hazardous wastes.

Page 84: Updated Initial Environmental Examination

71

Potential Impact Options for prevention or mitigation or enhancement

(f) Store hazardous construction materials in appropriately contained and elevated area and at least100 m away from surface water bodies.

(g) Have equipment clearly leaking oil repaired off-site immediately. No vehicle/equipment maintenance, repair and refuelling to be allowed at the sites.

(h) Treat construction water before discharge. Install water treatment plant for water generated during tunnel excavation. Allow water through grease trap or oil/collector and/or filters such as rock filled bags, block and gravel.

(i) Implement corrective action, when trigger thresholds of water quality are reached.

(j) During construction, the contractor shall take corrective action to reduce concentration to below the standard.

(k) Mitigating sedimentation (l) Use any combination of perimeter controls at

spoil disposal areas or stockpiles of aggregate materials, e.g., silt fences, sediment basins, sandbags, earth bern/bund.

Minimize / control dewatering or extraction of tunnel water by storing and re-using pumped-out water from the tunnel.

Performance Standard

Water Column. Parameters to characterize the physico-chemical and biological status of the water column to include but not limited to: temperature, salinity, total suspended solids, turbidity, dissolved oxygen and bacteriological parameters.

Refer to DAO 2016-08 for water quality standards

Extraction of water from Basin 1 (near the outlet) to be used as coolant during construction

Relevant permits to be secured.

Performance standard

If significant amount of water is to be used, a permit from the National Water Resources Board may be necessary.

DAO 2016-08 for water quality standards

Impact on groundwater:

(a) deteriorating shallow groundwater quality due to:

Silt/sediments

In all active work sites

Site temporary stockpile of excavated soils in flat areas, away from main surface drainage routes, limit to maximum of 2 m high.

Page 85: Updated Initial Environmental Examination

72

Potential Impact Options for prevention or mitigation or enhancement

Solid waste

Hazardous materials and waste Provide silt fences, silt traps, or sand bags, at stockpiles of aggregate materials.

Dispose of residual soil/spoil as soon as possible, to the disposal areas, or as free backfilling materials for LGU/barangay roads.

Avoid stockpiling more aggregates than necessary.

Performance Standard

DAO 1994- 26A for Philippine drinking water quality standards

(b) lowering of water level of wells in nearby communities due to tunnelling, pumping/extracting of tunnel drainage water

Monitor for potential groundwater depletion in existing wells in the vicinity. Provide interim measures to avoid disrupting water supply to affected households. Investigate for proper corrective action.

OPERATION PHASE

Potential impact in an El Nino event. Decrease of water for irrigation and domestic use.

El Nino related plans are in place and a Task Force was organized which includes MWSS.

El Nino Preparedness Plan drafted by NWRB is in place and was coordinated to concerned agencies including MWSS and its concessionaires (MWCI and MWSI). The Action Plans on Water Resources in Provinces to be Affected by El Nino (2015-2016) includes the following:

(a) Creation of El Nino Domestic Supply Management Task Force – composed of NWRB, MWSS, NIA, Maynilad, Manila Water was organized. The Task Force prepared as early as 2015 the guidelines for the allocation of water to ensure enough supply for everyone in Luzon (and also for Visayas and Mindanao).

(b) Reduced allocation for Metro Manila Water Supply from 41 to 38 cms and allocation of 10 cms for Irrigation (as of November 2, 2015)

(c) Consider granting temporary permits for the re-opening of closed and sealed deepwells in coordination with MWSS and DOH

(d) Draft Administrative Order for all Government Institutions to implement water conservation measures

(e) Conduct aggressive campaign on water conservation and coordination with Metro Manila

Page 86: Updated Initial Environmental Examination

73

Potential Impact Options for prevention or mitigation or enhancement

LGUs to mitigate the impacts (conducted meeting with LGUs last September 10, 2015)

Action Plans on Water Resources in Provinces to be Affected by El Nino

For Irrigation, grant temporary permits for the operation of shallow tube wells and small water impounding facilities.

For Water Utilities/Service Providers (CPC Grantees), prepare water conservation measures and submit the program to NWRB.

(a) Conduct advocacy campaign on water conservation

(b) Repair of leaks in the system and reduce non-revenue water

(c) Moratorium on increase in tariffs/water fees

5.4. People

Table 31: Potential Impacts on People

Potential Impact Options for prevention or mitigation or enhancement

PRE-CONSTRUCTION PHASE

Relocation of Families

During the conduct of consultations, three (3) families were identified residing within the MWSS portion of land that will be affected by the construction of the access road at the Ipo area. The head of the family used to be employed by MWSS as a security guard and later as Bantay Gubat, which eventually gave him the privilege to settle temporarily within the MWSS facilities. Moreover, one of the female spouses belongs to Dumagat tribe, as identified by the local NCIP Office in Angat.

Consultations were conducted to discuss the relocation of these families and corresponding compensation of structures. These consultations resulted to the payment of Php 30,000.00 compensation (computed based on the prevailing minimum wage used as payment for the lost days as stipulated on the Urban Development and Housing, or Act RA7279), to each family. Also, an additional Php 10,000.00 for each family was given. The determination of said amount has no legal basis; it was given as extra money for transportation for relocation expenses and is treated as “assistance.”

One of the family heads was successfully referred for employment with a local contractor. The affected families filed their application for three (3) housing units at the National Housing Authority.

The two (2) families, Gregorio Delos Santos and Realiza DS. Paray, were temporarily relocated at Ipo Road, San Mateo, Norzagaray, Bulacan, where they are renting a house. Ruel Delos Santos built a nipa hut just beside the compound of Angat Hydro Electric Power Plant, Norzagaray, Bulacan. Their National Housing Authority application for permanent relocation is now on process.

Page 87: Updated Initial Environmental Examination

74

Potential Impact Options for prevention or mitigation or enhancement

Affect the Indigenous People in the area

(a) Transport of students and residents as well as goods and services may be disturbed temporarily during construction due to temporary closure of boat landing on the other side of the Ipo Dam.

(b) May affect social activities, such as bathing and clothes washing among IPs downstream of the Ipo Dam spillway during construction due to possible water turbidity due to diggings.

(a) An alternative boat landing has already been identified upstream at the mouth of Sapang Munti River, half-a-kilometer away from the construction site to facilitate transport of people, students, goods, and services to ensure that the transport of residents undertaking socio-economic activities will be continuous even during construction.

(b) Ensure the access of IPs to river for bathing and clothes washing activities.

(c) An alternative route has been identified by the IPs and it will be improved by contractor to enhance safety of students and other residents using it.

(d) Formulation of IP Plan

CONSTRUCTION PHASE

Employment and Business Opportunities (a) The TBM tunnelling method will have higher advance rate. For mechanized tunnel methodology such as TBM, the employment requirement is less compared to the drill and blast tunnelling method.

Movement and accessibility.

(a) Increase road traffic due to inadequate capacity of Ipo Road (access road) and expected increase of truck volume

(b) Restricted access in active sites (c) Potential damage of existing

roads used as access roads due to movement of heavy equipment and vehicles

(a) Provision of alternative routes/ roads in Bigte area, fish landing sites in Ipo dam sites to allow continued movement and interaction.

(b) Consultation with residents of Brgy Bigte and Brgy San Mateo on possible temporary closure of current access roads, potential active sites during construction and alternative routes

(c) Establish alternate boat landing at the mouth of Sapang Munti River

(d) Institute prior coordination with the Barangay and Municipality for the formulation of a traffic management and safety plan and for clearing of structures encroaching into access road ROW.

(e) Prior to construction, clear easement of encroaching structures especially in along Ipo Road approaching the Ipo Dam Compound, mostly are being temporary.

(f) Strategically post billboards informing the public about the expected increase in volume of traffic in the influence area due to Project implementation. Post at least two weeks prior to mobilization.

(g) Coordinate with the Barangay for assistance in traffic management.

(h) Strategically post traffic flagmen along Ipo Road, equipped with two-way radio.

(i) Post sufficiently legible (reflectorized) traffic safety notice and signage at strategic locations along the entire stretch of the access road.

(j) Limit speed to 40 kph along Ipo Road, 20 kph at highly populated sections of Ipo Road, and 30 kph at construction sites and unpaved haulage roads.

(k) Coordinate with DPWH regarding the use of Ipo Road.

Page 88: Updated Initial Environmental Examination

75

Potential Impact Options for prevention or mitigation or enhancement (l) Restore access roads to the pre-construction condition or

better.

Performance Indicator

Zero road accident and related incidents

Community health and safety hazards potential health risks for persons with chronic disease such as asthma, and other respiratory diseases due dust pollution within the vicinity of the construction site and along road side

(a) Inform local residents of the timing of delivery of segmental lining, transport of oversized heavy equipment at the outlet and prohibit entry of local residents into the construction area.

(b) Secure project area, including associated facilities, from unauthorized entry.

(c) Implement measures to mitigate impacts on air and water quality, noise, traffic.

(d) Provide mechanism to reduce dust /other pollutants (i.e. water spraying on the road, transport of heavy equipment, segmental lining and spoil/excavated materials during day time, etc.)

(e) People with impaired health/risks wear masks and other protective device

(f) Ensure all systems for air, water, noise and land pollution are properly implemented

Workers’ health and safety hazard (a) Improved safety. There is no use of explosives for the TBM tunnelling method.

(b) Provision of adequate housing, amenities, sanitary facilities and sufficiently equipped emergency first-response and health care team linked to an ultimate response team.

OPERATIONAL PHASE

Public safety related to future development and activities along the ROW

MWSS must secure the ROW. Existing above ground infrastructure along ROW should be limited. The public must not be allowed to encroach onto the ROW by constructing any buildings or farming the land.

Security of tunnel 4

Potential encroachment of informal settlers along the 8 ROW, 6.4 Km alignment

(a) Conduct IEC on how to ensure security of tunnel 4 (b) Continuous monitoring of the ROW alignment for potential

encroachers (c) Fencing of the 60m ROW (a property of MWSS with land

title where as a titled property, trespassing is not allowed) where tunnel 4 is located. The fencing activity will be done after Tunnel 4 is constructed. No fencing will be done without the approval of NPC in the Tunnel 4 alignment that traversed Angat Watershed. Fencing of ROW might restrict access of farmers to the Ipo Road with fields southwest of the MWSS ROW. At present, due to rolling terrain of the area, only few areas are grown with agricultural products such as rice, corn and few fruit trees. Details of fencing is not yet available at this time. The design which will be done after the project should consider access of residents/ farmers.

(d) Incentives /imposition of penalty for encroachers

Page 89: Updated Initial Environmental Examination

76

VI. Environmental Management Plan

6.1. Introduction

142. The environmental management plan (EMP) will serve as the framework for the Project’s environmental management, commencing before the procurement process for CMC di Ravenna up to the operation. The EMPs will be mainly implemented by the Consulting Firm of AWTIP and the PMO, CMC di Ravenna and the Concessionaires. The EMP features the Environmental Mitigation Plan, Environmental Monitoring Plan, Implementation Arrangements and Performance Indicators.

6.2. Environmental Mitigation Plan

143. The recommended mitigation measures consist of actions, activities, plans and documents that need to be undertaken, observed, obtained, prepare to prevent and/or mitigate the Project’s adverse environmental impacts. The broad measures are outlined below while the specific measures are presented in the Environmental Mitigation Plan.

a) Ensure adequate considerations and conditions relative to climate change and other natural hazards to sustain the structural integrity and effective operations of completed works during project implementation.

b) Ensure engagement of an environment-responsible contractor, CMC di Ravenna, by incorporating the SPS-compliant EMP for this Project (hereinafter referred to as the EMP) into the bidding documents, as basis in the preparation of the Contractor’s EMP (CEMMP) by CMC di Ravenna, addressing as minimum the requirements of EMP. CEMMP to be quantitatively and qualitatively evaluated against the EMP by PMO-AWTIP and cleared by ADB prior to the commencement of any work onsite. The contract for civil works to explicitly stipulate the obligation to institute the mitigation measures properly and carry out environmental monitoring according to the CEMMP. The Contract to stipulate some tie-up of progress payment and collection of performance bond with the performance in CEMMP implementation.

c) A CEMMP that ensures good and environment-friendly engineering practices that avoid first, and (if unavoidable) mitigate, adverse impacts; and commitment from CMC di Ravenna to fully implement the CEMMP.

d) Quality construction supervision and environmental monitoring by the PMO-AWTIP.

e) Conduct of engineering investigations of built structures after every seismic, extreme weather and other natural hazard events during construction and operation and full disclosure of investigation reports. Prompt action to correct damages.

f) Sufficient funds for sustained quality of operation and maintenance. g) Observance of the grievance redress mechanism and prompt action/ resolution

of lodged grievances.

Page 90: Updated Initial Environmental Examination

77

Table 32: EMP prior to Construction Phase

Potential Impact

Possible approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible Performance Standard Guarantee

Required permits/ clearances

Obtain the following prior to Notice of Award:

a) ECC b) MOA between DENR RO 3, NPC and

MWSS c) Permit to cut tree d) Permit to use explosives for construction

a) PhP 500,000.00 b) none c) part of construction cost d) part of construction cost

a) MWSS b) MWSS c) CMC di

Ravenna

Permits/clearances obtained prior to Notice of Award

Employer’s requirement document

Preparing relevant communities

Conduct intensive social and environmental awareness program at least one month prior to Notice of Award, covering (i) communicable/ transmittable diseases that may be brought with the entry of workers; (ii) potential social conflicts between communities and workers; (iii) other health and safety hazards and impacts during construction and during maintenance and repair of completed works; and (iv) the grievance redress mechanism.

Included in PMO-AWTIP’s budget

PMO-AWTIP

Affected barangays

Ensuring environmentally responsible procurement

Include an SPS-compliant EMP in the bidding documents.

Not applicable PMO-AWTIP SPS-compliant EMP included in eth bidding documents

Append EMP to the Contract for basis in the preparation of the CEMMP.

PMO-AWTIP EMP appended in Contract

Page 91: Updated Initial Environmental Examination

78

In Contract, require CMC di Ravenna to submit monthly and semi-annual environmental monitoring report.

PMO-AWTIP Requirement stated in Contract

Stipulate in Contract the tie up of progress payment and collection of performance bond with the performance in CEMMP implementation.

PMO-AWTIP Stipulation in Contract

Prepare CEMMP that addresses as minimum the requirements of the EMP.

CMC di Ravenna Presence of a CEMMP based on EMP

Evaluate the CEMMP quantitatively and qualitatively against the EMP.

PMO-AWTIP Evaluation undertaken quantitatively and qualitatively

Clear the CEMMP before the start of any activity/work on site or establishment of any construction-related facility on site by CMC di Ravenna.

ADB CEMMP cleared prior to start of any mobilization activity on site by CMC di Ravenna

Page 92: Updated Initial Environmental Examination

79

Table 33: EMP for the Construction Phase

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

THE LAND

Soil and Erosion due to:

soil disturbance vegetation clearing

Location: Inlet structure and relevant work sites

Confine soil disturbance and/or vegetation clearing to pre-defined and planned area that includes project footprint and needed easements

Stabilize exposed soils with temporary seeding, mulches, mats, non-chemical-based soil binders.

Protect slopes with any one or combination of bonded fiber matrices, erosion control blankets, silt fence, fiber rolls, and keeping storm water off the slopes through diversion channels and/or berms.

Re-vegetate disturbed soils/slopes as soon as possible after completion of the construction works.

Replacing vegetation that died during the defects liability period.

Part of project development cost

CMC di Ravenna

PMO-AWTIP

CEMP

At the active work sites,

Provide temporary drainage with sedimentation tank or filters such as block and gravel, prior to discharge to watercourses

Loss of vegetation due to:

vegetation clearing and potential trampling of trucks/equipment

Institute measures to avoid impacting on habitats and wildlife, such as:

minimize vegetation clearance at Bigte and especially at the intake

fence off vegetation to be retained provide environmental training for workforce

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

Minimal number of trees applied for tree cutting permit from DENR

Tree cutting permit

Page 93: Updated Initial Environmental Examination

80

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

beyond project footprints

enforce site rules and sanctions to discourage workforce from hunting, fishing and poaching.

Confine all construction activities to previously disturbed areas, to the extent practicable, e.g., workers’ quarters/camps.

Use existing roads for project activities. Minimize new road construction.

To avoid unnecessary clearing, mark/delineate areas to be cleared of vegetation, e.g. by fencing.

Rehabilitate cleared areas to their pre-project conditions, unless otherwise agreed with the landowner.

Re-vegetate construction sites using local, indigenous species.

Re-vegetate watershed target sites especially in areas identified by the Watershed Management Plan.

Limit any collection of wood for charcoal to exotic i.e. non-native species.

Disturbance to wildlife due to

Construction noise, vibration, dust, lighting, presence/movement of people, etc.

Implement measures to mitigate noise, vibration and dust.

Strategically place nets at the tunnel portals to prevent flying debris.

Water to minimize dust accumulation and spreading.

Part of project (construction) cost

CMC di Ravenna PMO Record of number of poaching and illegal trading of wildlife by workers

N/A

THE WATER

Impact on surface water quality due to/ from:

At the active work sites

Mitigating contaminants

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

Water Column. Parameters to characterize the physico-chemical and biological

Page 94: Updated Initial Environmental Examination

81

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

Contaminants from materials used and construction activities and processes

Siltation from soil erosion, spoil disposal area, mechanical excavation, dewatering excavations, etc

Provide adequate sanitation facilities and water supply at work sites and workers’ camp. Enforce observance of good sanitation practices by workers.

Implement solid waste management that

minimizes, re-uses, properly segregates and promptly and properly disposes of generated solid wastes.

Implement hazardous waste management

that minimizes, properly segregates and promptly and properly disposes of generated hazardous wastes.

Store hazardous construction materials in

appropriately contained and elevated area and at least100 m away from surface water bodies.

Have equipment clearly leaking oil repaired

off-site immediately. No vehicle/equipment maintenance, repair and refuelling to be allowed at the sites.

Treat construction water before discharge.

Install settling pond for water generated during mechanical excavation. Allow water through grease trap or oil/collector and/or filters such as rock filled bags, block and gravel.

Implement corrective action, when trigger thresholds of water quality are reached.

During construction, the contractor shall take corrective action to reduce concentration to below the standard.

Mitigating sedimentation

status of the water column to include but not limited to: temperature, salinity, total suspended solids, turbidity, dissolved oxygen and bacteriological parameters.

Refer to DENR Administrative Order No. 2016-08, Water Quality Guidelines and General Effluent Standards of 2016

Page 95: Updated Initial Environmental Examination

82

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

Build cofferdams when constructing inlet structure

Use any combination of perimeter controls at spoil disposal areas or stockpiles of aggregate materials, e.g., silt fences, sediment basins, sandbags, earth bern/bund.

Minimize / control dewatering or extraction of tunnel water by storing and re-using pumped-out water from the tunnel.

Extraction of water from the dam site (inlet) and creek (near the outlet) to be used as coolant during construction

Use efficient tunnelling technology that recycles tunnel drainage water to minimize extraction of water.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

If significant amount of water is to be used, a permit from the National Water Resources Board may be necessary.

DENR Administrative Order No. 2016-08, Water Quality Guidelines and General Effluent Standards of 2016

Impact on groundwater:

a) deteriorating water quality due to: Silt/sediments Solid waste Hazardous

materials and waste

In all active work sites

Site temporary stockpile of excavated soils in flat areas, away from main surface drainage routes, limit to maximum of 4 m high.

Provide silt fences, silt traps, or sand bags, at stockpiles of aggregate materials.

Dispose of residual soil/spoil as soon as possible, to the disposal areas, or as free backfilling materials for LGU/barangay roads.

Avoid stockpiling more aggregates than necessary.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

DAO 1994- 26A for Philippine drinking water quality standards

Page 96: Updated Initial Environmental Examination

83

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

b) lowering of water level of wells in nearby communities due to tunnelling, pumping/extracting of tunnel drainage water

Monitor for potential groundwater depletion in existing wells in the vicinity. Provide interim measures to avoid disrupting water supply to affected households. Investigate for proper corrective action.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

THE AIR

b) Deterioration of ambient air quality due to dust and gas emissions from: Earthworks and

other construction processes; mechanical tunnelling;

stockpiling of aggregates and spoils, and conveyance of spoils to disposal areas;

increased transport activities in the construction areas and along Ipo Road;

At the project area, locate emission sources away from sensitive receptors, e.g., concrete batching and rock crushing plants at least 500m upwind of sensitive receptors.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

Maintain air quality within national air quality standards (NPCC 1980), or if these are not available, internationally accepted air quality standards, such as WHO Air Quality Guidelines Global Update, 2005

Parameter Averaging

Period Guide µg/m3

SO2 24 hrs 20

NO2 1 year

1 hour

40

200

PM10 1 year

24 hrs

20

50

PM2.5 1 year

24 hrs

10

25

CMC di Ravenna Scope of Work

CMC di Ravenna’s CEMMP

In active work sites:

Apply dust suppression techniques, e.g., watering with bowsers, sheeting particularly at Bigte area

Water dry unpaved/exposed surfaces, stockpiles of sand and excavated materials, at least twice daily, or as necessary.

Protect aggregate stockpiles with sheeting to restrict the movement of dust.

Require trucks, particularly those hauling aggregates, to have secure covers.

Limit engine idling to 5 minutes.

Prohibit open burning of vegetation and other waste in the project area

Page 97: Updated Initial Environmental Examination

84

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

burning of vegetation and wastes; and

operation of mechanical equipment

Ipo Road, main access road, other roads in the Project area,

Limit speed of all construction vehicles to max. of 40 kph on the access road to, and max. 30 kph in, the site.

Noise and vibration in the project area from drilling and general construction activities, vehicle and equipment operations

Use only equipment that emit least noise and vibration and are well maintained.

Use facility layout to minimize noise propagation e.g. using topography / existing buildings as barriers, where possible locate noisy activities away from local communities.

Control noise at source, e.g. low noise plant, muffling, acoustic screening, switch off campaigns.

Restrict use of noisy and highly vibrating equipment from 8AM-5PM. Necessary overtime work should: a) not go beyond 9:00PM; b) observe regulated noise and vibration levels; c) not use noisy and highly vibrating equipment; and d) should be coordinated with the barangay and affected households.

Manage the ins and outs of hauling trucks. Spread out the schedule of material, waste and spoil transport in the day (off-peak hours).

Enforce the rule of no blowing of horns.

Strictly enforce upon workers the compliance with wearing of ear mufflers, especially those who are operating equipment.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

Adopt national standards for construction sites and residential areas (NPCC, 1980). Alternatively use internationally accepted standards such as WHO.

Reference / Jurisdiction

Ambient Standard

Guidelines for Community Noise, WHO, 1999

International

Receptor: Residential; institutional; educational

Daytime (07:00-22:00): 55dBA

Nighttime (22:00-07:00): 45dBA

Receptor: Industrial; commercial

70dBA throughout the day

CMC di Ravenna Scope of Work

CMC di Ravenna’s CEM

MP

THE PEOPLE

Page 98: Updated Initial Environmental Examination

85

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

Involuntary Resettlement

Formulation of Involuntary Resettlement Plan

Compensation of the Project Affected Families

Part of the Project Cost

MWSS Appropriate

compensation and social assistance

Provision of livelihood activities for IP and Non IP affected families Part of Contract Cost MWSS / CMC di

Ravenna

Traffic due to:

inadequate capacity of Ipo Road (access road)

expected volume of truck movement

Institute prior coordination with the Barangay and Municipality for the formulation of a traffic management and safety plan and for clearing of structures encroaching into access road ROW.

Prior to construction, clear easement of encroaching structures, most of them being temporary.

Strategically post billboards informing the public about the expected increase in volume of traffic in the influence area due to Project implementation. Post at least two weeks prior to mobilization.

Coordinate with the Barangay for assistance in traffic management.

Strategically post traffic flagmen along Ipo Road, equipped with two-way radio.

Post sufficiently legible (reflectorized) traffic safety notice and signage at strategic locations along the entire stretch of the access road.

Limit speed to 40 kph along Ipo Road, and 30 kph at construction sites and unpaved haulage roads.

Part of project (construction) cost

CMC di Ravenna/ MWSS

Zero road accident and related incidents

CMC di Ravenna Scope of Work

CMC di Ravenna’s CEMMP

Page 99: Updated Initial Environmental Examination

86

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

Potential damage of existing roads used as access roads due to movement of heavy equipment and vehicles

Coordinate with DPWH regarding the use of Ipo Road.

Restore access roads within the MWSS compound to the pre-construction condition or better.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

CMC di Ravenna Scope of Work

CMC di Ravenna’s CEMP

Restricted access to the existing fish landing sites in Sitio Consultant (identified area as the Contractor’s Work Area) and boat landing at Sitio Ipo

Inform affected communities living in Ipo Watershed on the impact of construction works on transportation and consult them for the best alternative route. Have alternative route and fish and boat landing sites ready for use prior to commencement of construction activities.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

CMC di Ravenna Scope of Work

CMC di Ravenna’s CEMP

Community health and safety hazards

Prohibit entry of local residents into the construction area.

Secure project area, including associated facilities particularly the storage for explosives, from unauthorized entry.

Implement measures to mitigate impacts on air and water quality, noise, traffic.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

CMC di Ravenna Scope of Work

CMC di Ravenna’s CEMP

Workers’ health and safety hazard

Set up a sufficiently equipped emergency first-response and health care team, linked to an ultimate response team.

Provide safe housing with adequate basic services.

Enforce use of protective wears when at work.

CMC di Ravenna PMO-AWTIP

Page 100: Updated Initial Environmental Examination

87

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

Conduct pre-mobilization orientation workshop on health and safety and emergency response and evacuation procedures.

Generation of spoil and spoil disposal. More than 150,000m3 is expected to be generated due to tunnelling works, which is about 190,000 m3 loose volume.

Prepare and implement a plan for the preparation of the spoil disposal areas.

Minimise the volume of spoil to be disposed of by re-use in backfilling of roads, and by offering as free filling materials to government projects needing backfill materials.

Disposal area must be confined to solid ground, of low ecological and agricultural value.

Disposal area must not occupy drainage lines and streams, and create an obstacle to streams or induced flooding.

Spoil heaps must be designed and shaped with stable side slopes and suitable drainage.

Spoils heaps must be compacted during the earthworks.

On complete, the spoil heaps must be covered with the original top soil from the site and re-vegetated

Part of project development cost

CMC di Ravenna

PMO-AWTIP

Detailed Engineering Design (DED) Scope of Work Detailed Engineering and Design Plans

Solid waste Implement an eco-friendly solid waste management at work sites and workers’ camp/s, which minimizes, re-uses, segregates and promptly disposes of generated solid waste.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

CMC di Ravenna Scope of Work

CMC di Ravenna’s CEMMP

Page 101: Updated Initial Environmental Examination

88

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

Hazardous waste

Locate stationary ground storage for hazardous waste at least 100 m away from water bodies, raised to min 1 ft above high flood level. Or, use mobile storage but should not be parked near water bodies.

Secure storage areas appropriately. Storage facilities must be able to contain spillage.

Dispose of waste promptly and appropriately.

The contractor shall be required to implement an appropriate hazardous waste management program. Storage of oil and grease used for the maintenance and operation of heavy equipment shall be properly built and maintained, to include bunded storage for the capacity of the containers plus 10%, and oil traps on drainage outfalls.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

Construction CMC di Ravenna Scope of Work CMC di Ravenna’s CEMMP

Public safety as related to future development and activities along the ROW

MWSS must secure the ROW. Existing above ground infrastructure along ROW should be limited. The public must not be allowed to encroach onto the ROW by constructing any buildings or farming the land.

Part of project (construction) cost

MWSS/ CPF Construction CMC di Ravenna Scope of Work CMC di Ravenna’s CEMMP

Chance finds of PCRs and UXOs

A suitably qualified organization or demining company should be required to survey and clear the construction area prior to any commencement of construction works. All recovered UXOs shall be turned over to AFP or PNP EOD (Explosives and Ordnance Disposal) Division.

Part of project (construction) cost

CMC di Ravenna PMO-AWTIP

Zero injury or fatality of personnel carrying out survey and disposal works Zero injury or property damage to nearby populations Zero injury to construction workers

Page 102: Updated Initial Environmental Examination

89

Potential Impact Possible Approach/ Mitigating Measures Cost of Mitigation/ Enhancement

Responsible

Performance Standard Guarantee

Implement Monitor

Implementation of a UXO awareness program should be done to reduce the safety risks to the surrounding community.

Any recovered PCR chance finds shall be reported and turned over to National Historical Commission or National Museum.

Page 103: Updated Initial Environmental Examination

90

Table 34: EMP for the Operations Phase

Potential Impact

Possible approach/ Mitigating Measures Cost of Mitigation/ enhancement

Responsible Performance Standard Guarantee

THE PEOPLE

Public safety as related to future development and activities along the ROW

MWSS must secure the ROW. Existing above ground infrastructure along ROW should be limited. The public must not be allowed to encroach onto the ROW by constructing any buildings or farming the land.

Part of project maintenance cost

MWSS

CPF (represented by 2 water

concessionaires -MWCI and

MWSI)

Concession agreement

THE WATER

Changes in hydrology along Angat River during dry season

During the operation phase, flows shall be monitored downstream of Ipo dam.

As practice in the Philippines, Ipo dam should maintain 10% riparian flow downstream of Ipo dam. This flow aims to allow migration of fish species and to maintain natural characteristics of the river downstream of Ipo dam.

MWSS

CPF (represented by 2 water

concessionaires -MWCI and

MWSI)

Page 104: Updated Initial Environmental Examination

91

6.3. Institutional Arrangement

6.3.1. Existing Arrangement

The MWSS organization includes a Project Management Office (PMO) that looks after the

implementation of its projects. The PMO falls under the Office of the Deputy Administrator for

Engineering and Technical Operations Group. This project will be managed by the Project

Management Office - Angat Water Transmission Improvement Project (see Figure 15). The

PMO-AWTIP includes the project manager and his administrative support staff, a construction

group as technical staff, the contractor, and the construction supervision consultant.

The Resettlement Group is within the Engineering and Project Management Department -

Support Services (EPMD-Support Services). Manila Water Company, Inc. (MWCI) and Maynilad

Water Services, Inc. (MWSI) have their own resettlement and monitoring team to assist MWSS

as embodied in the Memorandum of Agreement (MOA).

MWSS has five consultants overseeing the implementation of the Watershed Management Plan

for Ipo watershed. The Consultants were previously employed by Bantay Kalisan, a non-

government organization of ABS-CBN Foundation, which was contracted by MWSS to manage

the Ipo watershed and draft the community-based Watershed Management Plan. The

implementation of the Ipo Watershed Management Plan includes tree planting, patrolling and

organizing the People’s Organization in the watershed. The People’s Organization is predominantly composed of the Dumagats, the indigenous group in Ipo watershed. The People’s Organization is funded by both Concessionaires through MWSS.

The two concessionaires, Manila Water Company Inc. (MWCI) and Maynilad Water Services Inc.

(MWSI), both have their own Environmental Department within their respective organizations.

These departments generally oversee environmental concerns of the operation of their

respective companies, including corporate social responsibility (CSR) activities.

The Common Purpose Facility (CPF) is composed of staff from MWCI and MWSI. The CPF

manages all infrastructures from Ipo dam, tunnels from Ipo to Bigte, Bigte portal Basins and

aqueducts from Bigte to La Mesa dam. The concessionaires’ staffs, assigned in the CPF, take

turns in being the head of the CPF.

Figure 20: MWSS Corporate Office Organizational Structure

Page 105: Updated Initial Environmental Examination

92

AWTIP

Project Implementation Officer

Project Manager

Construction

GroupSafeguard

Specialists

Social Safeguard

Specialist

Environmental

Specialist

Contract Supervision

Construction

Consultants

Safeguard

Specialists

Social Safeguard

Specialist

Environmental

Specialist

6.3.2. Proposed Arrangements for Environmental Management

For a more-focused management of social and environmental safeguard concerns of the project, it is proposed that a Safeguards Group (SG) be set up within the AWTIP PMO through its Consulting Firm. The SG will have its own social safeguard officer and Environmental Officer (EO) which the MWSS envisioned to provide for this project. The EO will handle the project’s environmental safeguard concerns/ environmental management. Qualified representations from the two concessionaires in the SG will be required at least 3 months prior to operation.

Figure 21 PMO-AWTIP with Consulting Firm

The following institutions are the key players for the environmental management of the Project

a) The MWSS, as the Executing Agency (EA) and the Implementing Agency (IA), for the project will be responsible for setting up of PMO; engaging an environmental officer for the PMO; facilitation the Multipartite Monitoring Team (MMT) as required by DAO 2017-15; and ensuring an environment responsible procurement of a CMC di Ravenna.

b) The Project Management Office together with the Consulting Firm for AWTIP (PMO-AWTIP), specifically the EO of its SG, will be responsible for overseeing the implementation of the Environmental Management Plan (EMP) and conditions

Page 106: Updated Initial Environmental Examination

93

prescribed in the Environmental Compliance Certificate.

c) Environment Safeguard Specialist for project implementation support will provide technical assistance and guidance to the AWTIP PMO, particularly its EO, in the implementation of the EMP and ECC conditions.

d) Social Safeguard Specialist for project implementation support will provide technical assistance and guidance to the AWTIPPMO, particularly its EO, in the implementation of the SDMP, IPP, SMRs and other social safeguards issues.

e) ADB will clear and approve any necessary revisions of the IEE and its EMP. ADB will clear/concur with any necessary IEE revision and/or EMP updating. Consequently, it will review environmental monitoring reports and undertake missions to review the environmental performance of the Project.

f) CMC di Ravenna incorporates the EMP prescribed environmental considerations in design and implements the EMP during detailed engineering design and during construction.

g) Concessionaires (MWCI and MWSI), as operators, will provide qualified environmental officers to work closely with the AWTIP PMO, commencing at least 3 months prior to construction, and implement the EMP and ECC conditions.

h) DENR/EMB Central Office will review and approve, respectively, the Project’s EIS and conduct review of the monitoring reports from the AWTIP PMO and MMT.

i) MMT will conduct the periodic monitoring prescribed in DAO 2017-15.

j) Local Government Units, namely the Municipality of Norzagaray (through its Municipal Planning and Development Office and Municipal Environmental and Natural Resources Office) and Barangays Bigte and San Mateo will provide representations in the MMT.

Page 107: Updated Initial Environmental Examination

94

Table 35: Institutional Responsibilities

Table 36: Institutional Responsibilities

Prior to construction During construction 10 During operation

MWSS Set up the PMO-AWTIP. Engage an Environmental Officer for the PMO-AWTIP.

Organize the Multipartite Monitoring Team (MMT)

Sign MOA with DENR and NPC on Angat Watershed and Forest Range Protected Area

Ensure an environmentally responsible procurement of a CMC di Ravenna.

Ensure an environmentally responsible maintenance policy

Review and endorse the CEMMP and the spoil management plan to ADB for approval.

Decide on environmental management matters requiring senior management intervention/action/ resolution.

Decide on environmental management matters requiring senior management intervention/action/ resolution.

PMO-AWTIP

(Assisted by the Consulting Firm)

Update IEE and EMP, as necessary.

Coordinate with CMC di Ravenna to ensure the incorporation of updated findings and mitigation

Measures in design and bidding documents.

Ensure EMP is part of the bidding documents, EMP clauses are incorporated in bidding documents, contracts.

Ensure DENR’s approval of EIS is granted prior to Notice of Award of D&B Contract.

Review CMC di Ravenna’s EMP (CEMMP) against EMP and the spoil management plan.

Endorse the CEMMP and spoil management plan to MWSS Management Team for ADB approval.

Conduct IEC, together with the Social Safeguard Officer in the PMO-AWTIP, for social preparation.

Ensure CMC di Ravenna has obtained permits for tree-cutting and use of explosive for construction not later than 3 days after receipt of Notice of Award.

Conduct inspections and spot checks to monitor the performance of the CMC di Ravenna in implementing the CEMMP/EMP

Review Monthly and semi-annual EMRs of CMC di Ravenna.

Submit the Semi-Annual EMRs prepared by CMC to ADB

Conduct inspections and spot checks to monitor the Performance of the Operator in implementing the EMP.

Review Monthly and Annual EMRs of Operator.

Prepare the Project’s Annual EMR for submission to ADB, until loan closure or as agreed.

Environmental Safeguard Specialist

(a member of Construction Supervision Team)

Provide technical assistance and guidance to PMO-AWTIP in the: - Update of IEE and EMP, as

necessary - Review of bidding documents * - Incorporation of environmental

criteria and weights in the evaluation of bids *

- Review of environmental aspects of bid documents *

Review of CEMMP against the SPS-compliant EMP

Provide technical advice/assistance e.g., preparation of Semi-annual EMR for ADB, review of results of environmental effects monitoring.

Page 108: Updated Initial Environmental Examination

95

Institution Prior to construction During construction During operation

Social Safeguards Specialist

(a member of Construction Supervision Team)

Provide technical assistance and guidance to PMO-AWTIP in the: Preparation of plans and programs (i.e. SDMP, IP Plan) for social safeguards Public Consultation and IEC Program for the project

Provide assistance and guidance in the monitoring of social safeguards implementation and compliance

ADB Review and clear updated IEE/EMP, if

applicable Approval of the Spoil Management Plan

and the CEMMP

Review Semi-annual EMR.

Review Annual EMR.

Design and Build (D&B) Contractor – CMC di Ravenna

Incorporate mitigation measures in design and bidding documents.

Incorporate EMP as part of bidding documents, EMP clauses in bidding documents, contracts.

Prepare a Contractor’s EMP that addresses as minimum the requirements of the EMP.

Obtain Tree-Cutting Permit and Permit to Use

Implement mitigation measures and conduct internal EMP implementation monitoring.

Conduct environmental quality monitoring as prescribed in SPS-compliant EMP. (If an independent Licensed Laboratory will not be engaged)

Prepare Monthly and Semi-annual EMRs.

Operators (MWSI and MWCI)

Ensure an environmentally responsible maintenance policy in congruence to MWSS maintenance policy

Perform maintenance works in accordance with the maintenance policy

Implement mitigation measures and conduct internal EMP implementation monitoring.

Prepare Monthly and Annual EMRs.

DENR Review and approve Project EIS.

Review MMT reports.

MMT Conduct

environmental monitoring in compliance With DAO 2017-15.

Municipality and Barangay Facilitate social preparation.

Participate in the MMT activities.

Participate in the monitoring of the performance of CMC di Ravenna in EMP implementation.

Facilitate (and participate in) public consultation/s and information disclosure

Review EMRs. Assist in ensuring

the observance of the GRM.

Participate in the monitoring of the performance of Operator in EMP implementation.

Facilitate (and participate in) public consultation/s and

information disclosure Review EMRs. Assist in ensuring the

observance of the GRM.

Page 109: Updated Initial Environmental Examination

96

6.3.3. Implementation Schedule

Environmental management will be implemented from the detailed design phase through to construction and operation. Table 37 presents the indicative time frame of key EMP activities in relation to Project implementation schedule.

Table 37: Environmental Management Implementation Schedule

Page 110: Updated Initial Environmental Examination

97

Activity Indicative Time Frame

PROJECT IMPLEMENTATION

CMC di Ravenna’s Mobilization Q1 Y1

Surveys and Investigations Q1 Y1

Detailed Design Q1 Y1 – Q2 Y1

Design Review and Approvals Q1 Y1 – Q3 Y1

Construction Q2 Y1 – Q2 Y5

Maintenance Period Q2 Y5 – Q2 Y6

ENVIRONMENTAL MANAGEMENT

Overall

1. Engagement of Environmental Specialist for project implementation support

Y0 (in place at least 2 months prior to bidding process for D&B starts)

2. PMO-AWTIP's submission of Environmental Monitoring Report (EMR)

- Monthly EMR for Project's Monthly Progress Report

8th day after effective month

- Semi-Annual EMR during D&B for submission to ADB

8th day after effective 6-mo. period

- Annual EMR for submission to ADB 8th day after effective year

- Self-monitoring report (DAO2017-15) 8th day after effective 6-mo. period

Prior to Notice of Award (NOA)/Notice to Proceed (NTP)

3. Secure MOA (in place of SAPA) Y0 - prior to EIS submission

4. Submit EIS for EMB CO review & secure approval from DENR CO

Y0 - prior to ICC application

BETWEEN NTP & PRIOR TO CONSTRUCTION MOBILIZATION

5. Inclusion of the EMP in the bid documents; obtaining ECC

Q4 Y0 (prior to Notice of Award)

6. Finalization of EMP, (if applicable) revision of IEE Q1 Y1 (ADB’s concurrence required prior to revision)

7. ADB review and approval of revised IEE and EMP. Q1 Y1

Page 111: Updated Initial Environmental Examination

98

Activity Indicative Time Frame

8. Community preparation (IEC, including disclosure of Final IEE and its EMP)

Q1 Y1

9. Preparation of CEMMP by selected CMC di Ravenna, review of CEMMP against SPS-compliant EMP, clearance from ADB

Q1 Y1, before start of works on site or establishment of construction- related facilities.

Construction Period (Mobilization to Demobilization)

10. Implementation of mitigation measures and conduct of environmental effects monitoring following the CEMMP.

Q2 Y1 – Q2 Y5

11. Submission of Environmental Monitoring Report (EMR)

Q3 Y2 – Q2 Y3

- Monthly, by CMC di Ravenna 5th day of the month following the effective month

- Semi-annually, by CMC di Ravenna 5th day of the month following the effective 6-month period

- Self-monitoring Report (DAO 2017-15 compliance), by PMO AWTIP

8th day after effective 6-month period

- Monitoring Report (DAO 2017-15 compliance) by MMT

Week 2 after the effective 6-month period

Operation Period (potentially could start even before Maintenance Period is over)

12. Implementation of mitigation measures and monitoring activities as specified in the EMP

Starting Q2 Y6

13. Submission of EMR Starting Q2 Y6

- Monthly, by Concessionaires 5th day of the month following the effective month

- Yearly, by Concessionaires 5th day after effective year

6.4. Environmental Monitoring Plan

152. Two types of monitoring are required -- environmental and compliance/ performance monitoring. Environmental effects monitoring will cover: (1) ambient air quality; (2) noise levels; (3) surface water quality; (4) terrestrial (flora and fauna) ecology; (5) river ecology; (6) community health and safety prior to construction and during construction and operation; and (7) workers’ health and safety during construction and operation (maintenance and repair). Compliance monitoring will monitor and evaluate the performance of the CMC di Ravenna, Concessionaire, and PMO-

Page 112: Updated Initial Environmental Examination

99

AWTIP in complying with, or adhering to, the CEMMP/EMP.

6.5.1. Monitoring Mechanism

153. A hierarchy of monitoring teams is presented below.

a) The base layer of monitoring will be done by the CMC di Ravenna to ensure that construction impacts on environment and its personnel are within the acceptable limits set in the CMC di Ravenna Environmental Management Plan (CEMP).

b) The second layer is the internal monitoring of CPF and MWSS. The monitoring is intended to provide information useful in promoting consistency and compliance with the Environmental Management Plan (EMP) and compliance with the ECC conditions and continued update of the EMP for sustained responsiveness to project construction, operations and impacts.

c) The third layer is an external monitoring by the multipartite monitoring team, which is composed of representatives of MWSS, CPF, Brgy San Mateo LGU, Brgy Bigte LGU, EMB CO, relevant government agencies. The Multipartite Monitoring Team (MMT) shall be organized to encourage public participation, to promote greater stakeholder vigilance and to provide the appropriate check and balance mechanisms in the monitoring of project implementation.

d) The fourth layer is an external monitoring by DENR. The monitoring is intended to check compliance to the ECC conditions and effectiveness of environmental measures

e) The fifth layer monitoring will be undertaken by ADB. This layer of monitoring is intended to ensure that construction and operation activities comply with ADB policies and safeguards.

f) Independent Monitoring Team is an external independent team to undertake independent audit and evaluate effectiveness of the environmental measures implemented by the contractor and the project’s operators (the concessionaires – MWCI and MWSI) to mitigate the environmental Project Impacts referred to in this IEE. The independent monitoring of the environmental measures shall be undertaken during construction phase and for the first five years of operation.

Page 113: Updated Initial Environmental Examination

100

Table 38: Composition of the Multipartite Monitoring Team

MMT Member Proposed Role Scope of Responsibility MENRO MMT chairman overall responsible in the monitoring activities and

reports of MMT MMT Co-

chairman assumes the responsibility of chairmanship in meetings and monitoring activities in the absence of the Chairman

(a) Brgy Captain of San Mateo, Federico Cruz (b) NWRB, Sevillo D

David Jr (c) Bigte Tanod

Chief, Dioscoro Madrid

MMT members for water quality

(a) To conduct water quality monitoring in quarterly basis and monitor the proponent and contractor’s water sampling activities; compliance to ECC and EMP

(b) Prepare report on water quality results and findings and submit to MMT Chair for review and comments

(a) Barangay Captain of Bigte, Jovina Lamadrid

(b) Brgy Bigte TODA President,

(c) San Mateo Kababaihan, Imelda Cristobal

MMT members for air quality

(c) To conduct air quality monitoring in quarterly/ semi-annual basis (wet and dry season) and monitor the proponent and contractor’s air sampling activities.

(d) Prepare report on air quality results and findings and submit to MMT Chair for review and comments

(d) NPC Senior Engineer, Randy David Monsanto

(e) Dumagat Chieftain, Ochie Aquino

MMT members for biodiversity

(e) To conduct biodiversity monitoring (flora and fauna) in semi-annual basis (wet and dry season) and monitor the proponent and contractor’s biodiversity monitoring activities.

(f) Prepare report on biodiversity survey results and findings and submit to MMT Chair for review and comments

(f) Municipal Health Officer, Dr. George Peppard Paitim

(g) NCIP Area Manager, Regina Panlillio

(h) NGO, (TBA)

MMT members for social

(g) To conduct social monitoring every year and monitor the proponent and contractor’s social monitoring activities.

(h) Prepare report on grievance case, socio economic survey, health and safety, public health results and findings and submit to MMT Chair for review and comments

154. Table 39 summarizes the proposed environmental monitoring plan, which identifies the main environmental aspects, the potential impact arising, the key parameters to be monitored, and the sampling and management plan. The monitoring plan focuses on the construction period

Page 114: Updated Initial Environmental Examination

101

as no significant environmental impacts were identified for the operations phase. Currently, MWSS carries out daily observations of the raw water quality at the inlet structure. Hence, it would not be necessary to have the same during the operation of Tunnel 4.

155. Existing conditions have been measured during the conduct of the first draft of IEE, 2014 July. The results may be adopted as the baseline conditions against which results of environmental effects monitoring during construction will be evaluated. The environmental monitoring plan covers water quality, air quality, construction noise, and vegetation monitoring.

156. The monitoring plan should be updated to reflect the DENR recommendation specified in the ECC. The bid documents for the procurement of CMC di Ravenna should include implementation of environmental measures and drafting of the CEMMP. This shall be submitted to MWSS for review and approval

Page 115: Updated Initial Environmental Examination

102

Table 39: Environmental Monitoring Plan

Potential Impacts per Environmental

Sector

Parameter to be Monitored

Sampling and Measurement Plan Lead Person Annual Estimated Cost

Method Frequency Location Indicate coordinates/description

of location

PRE-CONSTRUCTION PHASE

The People Social and environmental awareness

IEC Consultation FGD

Note: These activities were done prior to project construction and shall be continued during construction and operation

Stakeholders/ residents near construction areas and tunnel ROW

MWSS

CONSTRUCTION PHASE

The Land

Loss and damage to terrestrial vegetation

Over-clearance and damage to vegetation around the construction sites

Vegetation cover Visual inspection pre-construction survey of vegetation at construction sites an stake out / fence off vegetation to be retained weekly monitoring of vegetation cove around construction sites, Monitoring of revegetation of temporary construction sites in accordance with the C-EMP requirements for the restoration of temporary construction sites.

construction areas where vegetation clearance is done

Environment specialist of the project

Page 116: Updated Initial Environmental Examination

103

The Water

Water quality Deterioration of

water quality in Ipo Darn and Bigte

River during construction

Extraction of water from Angat River

above the allowable volume (water

rights)

Temperature

pH

Conductivity

Total Suspended Solids

DO

BOD5

Oil and Grease

Total Coliform

Faecal Coliform

Refer to DAO 2016-08

Grab sampling; RA 9275 lab analysis method

Refer to DAO 2016-08

Monthly water quality sampling to include wet and dry seasons. After every accidental spillage event. Daily observations of water quality. 2 per month water quality sampling to include wet and dry seasons. After every accidental spillage event.

Angat River Upper Reach Upstream Ipo Dam (N14 53’ 41.6’’; E121 10’ 10.8’’) Ipo Dam Site (in the vicinity of construction area, near the intake of Tunnel 1,2 and 3) (N14 52’ 23.5’’; E121 10’ 0.08’’)

Downstream Ipo Dam (N14 52’ 36.8’’; E121 10’ 42.3’’) Bigte Upstream Bigte Tributary Sitio settling ( N14 51.538 E121 05.543) Bigte river (N14 50.431 E121 05.453) Sta. Maria River (N14 50.066 E121 04.563)

Project Environment specialist

P 100/ sample*2 bottle/ station/ quarter*4 quarters/ yr. = P800

P60/ sample*2 bottle/ station/ quarter*4 quarters/ yr. = P 480

P230/ sample*2 bottle/ station/ quarter*4 quarters/ yr. = P1840

P500/ sample*2 bottle/ station/ month*12 mos./yr. = P12,000

P345/ sample*2 bottle/ station/ quarter*4 quarters/ yr. = P2760

P800/ sample*1 sample/ month*12 mos./ yr. = P9,600

P700/ sample* 1 sample/ month* 12 mos./ yr. = P8,400

P990/ sample* 1 sample/ month* 12

750 MPN/ 100 mL

P500/ sample* 1 sample/ month* 12 mos./ yr. = P6,000

Volume of water extracted from Angat River (Ipo Dam) Please note that the current allowable water rights (from Angat reservoir = 46 m3/s; from flows from Umiray = 4 m3/s; Ipo catchment between the Angat and Ipo dams = 2 m3/s.

Flow meter to be installed at the intake in Ipo dam

daily Ipo Dam Intake MWSS Included in the operation cost

Page 117: Updated Initial Environmental Examination

104

The Air The air deterioration of ambient air quality during construction

Where haulage exceeds 200 heavy

goods vehicle (HGV) per day

Air quality in the tunnel

Construction Noise

Increase noise levels due to (a)

blasting, (b) general construction

activities, and (c) haulage traffic

Dust deposition (Total Suspended Particulates)

See recommended methods for sampling in testing of ambient air parameters stated in DAO 2000-81

a) Pre-construction monthly dust deposition monitoring b) Monthly monitoring during construction

Ipo Dam Site Brgy Hall of San Mateo MWSS Bigte Portal And/or any haul routes on unpaved roads near communities.

Project environment specialist

P65,000/ 3 sampling sites for ambient air quality and noise* 12 mos./ yr. = P780,000

NOx See recommended methods for sampling in testing of ambient air parameters stated in DAO 2000-81

Monthly analysis while construction traffic exceeds 200 HGVs / day

At a sample of villages along haul roads caring more than 200 HGVs/ day

Oxygen and Carbon monoxide

BS6164 Construction: 2011 Throughout the tunnelling construction Continuous monitoring of oxygen with equipment conforming to BS EN 50104

Direct monitoring of carbon dioxide within tunnel.

Average ambient noise levels LAeq Maximum noise levels LAeqmax

Direct read out Minimum of 15 minute measurements at different times of the working day and at night in the event of night-time working. (a)Pre-construction /CWA) baseline at all the construction sites an main haul roads and a selection of potential receptors nearby (b) Monthly monitoring at all the construction sites, Including camps, spoil disposal areas, and along the main haulage roads and a selection of potential receptors nearby. (c) Following complaints from local communities at the complainant's property and on the nearby construction sites.

Ipo Dam site (Construction site/ CWA) Brgy Hall of San Mateo MWSS Bigte Portal (Construction Site/ CWA)

Page 118: Updated Initial Environmental Examination

105

The people Public health and safety Socio-economic indicators (identification and assessment of the socio-economic impacts of the construction activities of the tunnel to Brgys Bigte and San Mateo) Socio economic indicators: populations; land and house ownership; household income; resettlement; livelihood; LGU income; electric power; social facilities and infrastructure; employment; and education. Assessment of potential health hazards and human health risks to Brgys Bigte and San Mateo to include the following: health impacts; morbidity; mortality; health facilities; environmental sanitation; health profile of Brgy Bigte and San Mateo; Vital health indices; malnutrition; and environmental quality and health

FGD

Interviews

Use of secondary data from Brgy health centres

annual Sitio Ipo, Sitio Copra, Sitio Anginan of Barangay San Mateo Sitio Upper, Sitio Spar Settling and Sitio Poblacion of Barangay Bigte

P450,000

OPERATIONAL PHASE

The Water Water quality

Deterioration of water quality in Ipo Darn

and Bigte River during construction

Temperature

pH

conductivity

Refer to DAO 2016-08

Grab sampling; RA 9275 lab analysis method

Monthly water quality sampling to include wet and dry seasons. After every accidental spillage event.

Angat River Upper Reach Upstream Ipo Dam (N14 53’ 41.6’’; E121 10’ 10.8’’) Ipo Dam Site (in the vicinity of

Project Environment specialist

P 100/ sample*2 bottle/ station/ quarter*4 quarters/ yr. = P800

P60/ sample*2 bottle/ station/ quarter*4 quarters/ yr. = P 480

Page 119: Updated Initial Environmental Examination

106

TSS

DO

BOD5

Oil and Grease

Total Coliform

Faecal Coliform

construction area, near the intake of Tunnel 1,2 and 3) (N14 52’ 23.5’’; E121 10’ 0.08’’)

Downstream Ipo Dam (N14 52’ 36.8’’; E121 10’ 42.3’’) Bigte Upstream Bigte Tributary Sitio settling ( N14 51.538 E121 05.543) Bigte river (N14 50.431 E121 05.453) Sta. Maria River (N14 50.066 E121 04.563)

P230/ sample*2 bottle/ station/ quarter*4 quarters/ yr. = P1840

P500/ sample*2 bottle/ station/ quarter*4 quarters/yr. = P4,000

P345/ sample*2 bottle/ station/ quarter*4 quarters/ yr. = P2760

P800/ sample*2 sample/ quarter*4 quarters/ yr. = P6,400

P700/ sample* 2 sample/ quarter* 4 quarters/ yr. = P5,600

P1035/ sample* 2 sample/ quarter* 4 quarters/ yr. = P8,280

P500/ sample* 2 sample/ quarter* 4 quarters/ yr. = P4,000

Page 120: Updated Initial Environmental Examination

107

6.6. 6.4.5. Reporting

157. Environmental monitoring activities and findings shall be documented for reporting, recording, verification, referral and evaluation of the environmental performance of the Project. The documentation shall also be used as basis in correcting and enhancing further environmental mitigation and monitoring.

158. Environmental Monitoring Reports (EMRs) shall be prepared as follows:

a) Monthly, by the CMC di Ravenna during detailed design and construction and by the Concessionaires during operation, to be submitted to the PMO-AWTIP, to include, at least: (1) physical progress of the Subproject; (2) mitigation measures implemented in line with the CEMMP/EMP; (3) grievances received, resolved, closed and those directed to other mechanisms; and (4) if any, engineering investigation and corrective actions after a seismic or extreme weather event. The monthly EMRs will be submitted to the PMO-AWTIP.

b) Monthly, by the PMO-AWTIP, incorporating the monthly reports of CMC di Ravenna or Concessionaires into the overall monthly progress report of Project. In addition, to include: (i) feedbacks from informal random interviews with affected communities; (iii) findings from regular inspections and unannounced spot checks; and assessment of the environmental performance of CMC di Ravenna or Concessionaires.

c) Semi-annually during detailed design and construction and annually during operation until loan closure or as agreed, by the PMO-AWTIP to be submitted to the ADB to fulfil the environmental agreement in the loan. The Semi-Annual EMRs will not only report on the progress and results of environmental monitoring and compliance of the CEMMP/EMP implementation but also: (1) assess the effectiveness of instituted measures; (2) point out violation/s, if any; (3) assess/recommend corrective actions; and (4) cite any coordination made for corrective actions and, if applicable, certifications for having instituted them effectively. It shall also feature any innovative mitigation measures applied by the CMC di Ravenna or Concessionaires, and other lessons learned in CEMMP/EMP implementation. These will be useful in adjusting the CEMMP/EMP to adapt to real ground situations. (Proposed adjustments/ enhancement of the CEMMP/EMP must have prior ADB clearance.)

159. The monthly EMRs by the CMC di Ravenna may adopt the outline, as applicable, to facilitate the preparation of the Semi-Annual EMRs. In compliance with the Revised Procedural Manual for DAO 2017-15 and addressing the conditions of ECC, the environmental monitoring reports shall be prepared as follows and submitted to EMB CO:

a) PMO- AWTIP, through its Consulting Firm shall prepare and submit Self-Monitoring Report to EMB CO quarterly basis following the outline prescribed in the Revised Procedural Manual for DAO 03-30.

b) MMT shall prepare Compliance Monitoring and Validation Report as the MMT Report Form on semi-annual basis.

Page 121: Updated Initial Environmental Examination

108

VII. Public Consultation, Information Disclosure and Grievance Redress Mechanism

7.2. Public Consultation

160. A series of consultation meetings were held with the communities, barangay councils of Brgy. San Mateo and Brgy. Bigte, NCIP, Dumagats, NGOs and Municipality of Norzagaray. The information about the project’s environmental issues and concerns and technical data of the project were discussed in Tagalog, a dialect which the locals and indigenous peoples (IP) can understand. In addition to the public consultation, focus group discussions were held with the IP communities. Flyers about the project was also distributed.

161. The following issues were raised during the first and second public consultations with Brgy. San Mateo, Brgy. Bigte and Dumagat communities.

Table 40: Summary of Public Consultation 2013 July and 2014 July

Issues, Concerns, Interests from Stakeholders MWSS (and consultants, NWRB) Response

Lack of domestic water supply in Brgys. Bigte and San Mateo.

Another MWSS project is underway and the feasibility of treated water distribution in Bulacan.

Identification of affected person (APs), especially the residents along MWSS ROW. Concerns on the process of demolition of properties (with land titles and illegal settlers) along MWSS ROW.

MWSS assures to have proper survey of the tunnel ROW before project commences. Affected residents will be compensated if relocation is needed.

Impacts on road safety due to increase in traffic and transportation of spoil from the construction site to temporary spoil disposal. Identification of the roads likely to be affected, especially during the construction phase.

The residents are aware that their houses and/ or their house plot fences have encroached in the ROW. The 1m road easement on both sides of the road is recognized by the residents. Mitigating measures on the potential impacts caused by the transportation of spoil will be included in the EMP With a possible mitigating measure.

Employment opportunities for the local population (Brgys. Bigte and San Mateo).

The community will be prioritized for jobs suitable to their acquired skills and capability.

Generation and management of spoil. Residents requested whether they could take the spoil for their personal use, e.g. as backfill material in their house plots. Spoil can also be used as community road backfill especially in dirt roads.

The residents’ request for spoil may be coursed through the barangay council and such consolidated request will be forwarded to MWSS/ Design and Build Contractor.

Commencement of the project construction. The project is expected to start in 2015. For the project to push through, several approvals are needed with the release of ADB loan.

The barangays are keen to having another consultation/ discussion on the project implementation prior to the start of construction.

Consultation meetings with affected communities will be conducted by MWSS prior to construction.

Determination of alternative routes and fish landing at Sitio Ipo.

Alternative route and boat landing should be identified prior to commencement of tunnel construction. Potential boat landing site was identified near the mouth of Sapang Munti, a tributary of Angat River near the dam site.

Page 122: Updated Initial Environmental Examination

109

Table 41: Summary of Public Consultation – 2016 August

Issues, Concerns, Interests from Stakeholders MWSS (and consultants, NWRB) Response

Mr. Frederico ‘Dadeng’ Cruz, Brgy Captain of Brgy San Mateo (in his opening remarks): lack of water supply in

Brgy San Mateo; water supply in host barangays

~This was noted by MWSS. MWSS

expressed that there are plans underway for

the community’s water supply.

The water being allocated to Metro Manila and nearby areas are coming from their community but the host community do not have water. They also have plans to have the constituents sign a petition and present it to MWSS. The main problem of the barangay is water considering that IPO Dam is located in the area. He hopes that the MWSS will soon have plans for water supply to their community.

Mr. Geronimo G Cristobal, Vice Mayor of the Municipality

of Norzagaray, Bulacan: water supply project in host

barangays

The Vice Mayor encouraged everyone to listen and be

aware of the project and even extend help I needed. He

stated that the project will not only help the nearby area

but also the neighbouring communities like Metro Manila.

He briefly mentioned about a well that they had was tested by the Norzagaray Water District but it is dry and that the land is of volcanic ash composition and there is no opportunity to create a deep well. Also expressed that the community of San Mateo is very lucky as the community will be host to the Tunnel 4 project. However, he is unhappy that the host barangay do not have

Water supply. He also mentioned about a deep well on the land of his kin Cruz’ of San Mateo and asked a Project Manager of the Norzagaray Water District for a pump out test. Initially, it was said that the deep well can supply up to 300 households, when they were to install the submersible pump, he was informed that the lower part of the land is skewed that instead of a 3-meter elevation, it is just half. So instead of servicing 300 households, the system can only supply 150 households.

He expressed that the local government unit does not have any capacity to fund a water supply project. He informed the audience that they then needed around Php60Million to fund the project and how small it is compared to the current AWTIP project of $3.2billion. He hopes that assistance could be extended to the community water supply project and hopefully after the project, the community will no longer have water issues.

~This was noted by MWSS.

MWSS discussed very brief

information about the

Bulacan Bulk Water Supply

Project.

Page 123: Updated Initial Environmental Examination

110

Mr. Gilbert, IPO Dam resident: domestic well near MWSS

Asked on advice on a well inside his property which is a

few meters away from MWSS’s right of way as this will be impacted most especially that he has livestock at his

property. The well is currently his source of water for

domestic use.

~Ms. Mildred, Socio-

economic Consultant of

MWSS, advised that as

Part of the ADB’s social safeguards this will be duly compensated. Also another advice to

secure a permit was given. That the best thing

to do for now is to secure a permit for the well

and to transfer it for now. An information that

an exemption to secure a permit for well’s is only for 6 people has also been provided.

~NWRB asked if such well had been secured

of a permit from NWRB. NWRB explained that

process by which a well is constructed and

should be secured of a permit from NWRB

IPO Dam resident: impact of the project to the creek as

domestic water source of the community

Raised an issue about a creek on the location of the

project as this is there water source for laundry and

washing the dishes.

~MWSS responded that this will not be

affected as the tunnel is below the ground and

the creek is above the ground and the water

flow on the tunnel will only come from the

water stored on the Dam. That the tunnels are

sealed and will not get water from any other

source.

Ms. Cora Canlas, resident from Sitio Copra of Brgy San

Mateo: other water sources for Brgy San Mateo

Raised a concern to separate the AWTIP project from the

current issue of the locals as 3 years completion is a long

wait time for them. She also conducted a study and

wanted to confirm some possible water sources in Sitio

Copra such as having reservoir in the area and this may

take 1 year at most.

~MWSS discussed about the Bulacan project

which will have a separate public consultation

like this and it has already been awarded to

San Miguel Corporation. So the community

will have to wait for the public consultation by

San Miguel for the Bulacan Bulk Project.

Mr Vanderleaf Capulungan, EIA Review Committee Chair: EIA information, IEC, Grievance Mechanism,

project activity funding. He encouraged everyone to raise their issues and concerns as early as now. He

showed the public a copy of EIA main report (Annexes not included) which he and his team are reviewing.

He informed everyone who needs to know information about the project and its impact can get a copy from

the barangay. The audience was advised that once ECC has been issued and all necessary permits

granted, this project will commence. As much as possible issues and concerns must be raised as there is

still safeguard for the people which is called grievance mechanism. All concerns must be raised so that

funds for such endeavour, activities can be appropriated accordingly.

Page 124: Updated Initial Environmental Examination

111

Summary of Public Consultation – 2018 June

162. The Metropolitan Waterworks and Sewerage System (MWSS), in coordination with the Local Government Unit (LGU) of Norzagaray, Bulacan, Barangay Officials, CMC di Ravenna (contractor) and ARUP (consultant), conducted a public consultation with the residents of Barangays San Mateo (135 attendees) and Bigte (69 attendees), Norzagaray, Bulacan on 1 June 2018. Another round of public consultation with the Indigenous Peoples (IPs) residing in Sitio Anginan/Pako/Santol, Sitio Sapang Munti, Sitio Ipo, Sitio Dyke, & other IP Communities from the Ipo Dam Area was carried out on 26 June 2018 to meet the following objectives:

1) To inform the public of the current project progress of the Angat Water Transmission

Improvement Project (AWTIP)

2) To educate the residents on the safety measures to be undertaken during the transport of heavy

equipment along the Ipo Road leading to Ipo Site (Construction of tunnel from Ipo to Bigte)

163. The technical details and progress of the project and the safety measures to be undertaken during the transport of Heavy Equipment along the Ipo Road were presented in a manner that is easily understood by the residents (local language) to encourage active participation in the proceedings, with the aid of a PowerPoint presentation. A video presentation on how the Tunnel Boring Machine (TBM) works to excavate tunnel with a circular cross section through a variety of soil and rock strata was also shown to the residents for them to have a better appreciation of the TBM. Some of the residents were seen taking pictures and videos of the presentation which showed their keen interest on the project.

164. The MWSS team also gave emphasis on the advantages of using TBMs compared to drill and blast (D & B):

1. The TBM has the ability of limiting the disturbance to the surrounding ground/areas and

producing a smooth tunnel wall, without open excavations

2. More efficient than drilling and blasting (D & B) which result to shortened completion times.

3. Safety considerations for the workers and the residents

165. The Project Team mentioned that as of 1 June 2018, the TBM has accomplished 1.04185 kms length of tunnel and the longest accomplishment in a day is pegged at 35 meters

166. The results of the Ipo Road inspection conducted on 26 April 2018 were also presented in the vernacular for the residents to have a better understanding of the Safety Measures / Traffic Management Plan.

Page 125: Updated Initial Environmental Examination

112

Public Consultation at Ipo Watershed, Norzagaray Bulacan

Things to consider in transporting heavy equipment

(Mga dapat ayusin sa paglilipat ng mga Heavy Equipment)

Impact Prospect Solution

(Mga kaukulang hakbang)

The Arc boundary of Brgy. Bigte and Brgy San Mateo in Norzagaray Bulacan which is made of concrete and steel. The Maximum height level that can pass through the arc is too low for heavy equipments.

(Ang Boundary Arc ng Brgy. Bigte at Brgy. San Mateo, Norzagaray, Bulacan ay masyadong mababa para makadaan ang mga heavy equipment. Ito ay gawa sa bakal at semento)

Very Low, Manageable

CMC di Ravenna to coordinate with the officials of the respective barangays.

(Makikipag-ugnayan ang CMC di Ravenna sa mga opisyal ng nabanggit na barangay)

Cable / Electrical Wires obstructions in the highway in particular locations such as:

In front of Lot No. 022, Sitio Compra.

Nearby Iglesia ni Cristo, Sitio Compra.

Nearby San Mateo Brgy. Hall

Residential Houses before IPO compound gate.

(Mababang kable ng kuryente sa mga sumusunod na lokasyon:

a. *Tapat ng Bahay na may Bilang 022

b. *Sitio Compra

c. *Iglesia ni Cristo

d. *San Mateo Barangay Hall * Kabahayan malapit sa Ipo Compound Gate)

Low, Manageable

CMC to coordinate with Electrical Power Supplier (MERALCO) regarding the situation and to inform them of the particular height/width/length of the heavy equipment which will be passing in the area for them to be able to arrange and fix the cable obstructions and/or temporary power outage in the area to secure the safety during the transport.

(Makikipag-ugnayan ang CMC di Ravenna sa MERALCO kaugnay sa sukat (laki/haba/lapad) ng mga heavy equipment para maiayos ang mga kable ng kuryente sa kahabaan ng Ipo Road at posibleng pansamantalang pagpapatigil sa daloy ng kuryente habang isinasagawa ang paglilipat para masiguro ang kaligtasan ng lahat)

Page 126: Updated Initial Environmental Examination

113

Temporary Structures built along the Ipo Road

(Mga pansamantalang istruktura sa kahabaan ng Ipo Road)

Low to medium MWSS will have indications on the boundary of their Right-of-Way (demarcation line).

MWSS and CMC di Ravenna to coordinate with the Local Government of Norzagaray, Bulacan for the conduction of consultation and information dissemination together with the residents along the stretch of Ipo Road.

(Maglalagay ang MWSS ng mga tanda (markers) para matukoy ang hangganan ng Right of Way ng MWSS (demarcation line)

Makikipag-ugnayan ang CMC di Ravenna at MWSS sa Lokal na Pamahalaan ng Norzagaray, Bulacan para sa konsultasyon / pakikipag-usap sa mga naninirahan sa kahabaan ng Ipo Road.)

Illegally parked vehicles along the Stretch of Ipo Road in particular along Hilltop Market in San Mateo, Norzagaray, Bulacan.

(Mga sasakyang nakaparada sa kahabaan ng Ipo Road, lalo na sa mga matataong lugar gaya ng Hilltop Market, San Mateo, Norzagaray, Bulacan)

Low to medium

Formulation or establishment of Traffic Management and Safety Plan of CMC di Ravenna in accordance with the rules and regulations implemented by the traffic management council of Norzagaray, Bulacan

Deployment of Traffic Personnel from the Local Government Office / Baranggay Office to assist in traffic control during transport of the heavy equipments.

Installation of additional Traffic Signs especially in critical/prone accidents areas and/or public places.

Implementation of Speed Limit of 40kph along IPO road and 10kph for the public places.

Page 127: Updated Initial Environmental Examination

114

(Pagbalangkas ng Traffic Management and Safety Plan ng CMC di Ravenna alinsunod sa mga batas-trapiko ng Lokal na Pamahalaan ng Norzagaray, Bulacan

Pagtatalaga ng Lokal na Pamahalaan ng mga Traffic Personnel at Barangay Tanod na mamahala sa daloy ng trapiko habang isinasagawa ang paglilipat ng mga heavy equipment

Paglalagay ng mga karagdagang traffic signs lalo na sa mga kritikal at mataong lugar

Paglimita ng tulin/takbo ng mga sasakyan sa 40 kph sa Ipo Road at 10 kph sa mga mataong lugar )

Specific dates / Schedule of transport of heavy equipment (to and from bigte) and Tunnel Boring Machine (from Ipo to Bigte)

(Nakatakdang araw ng paglilipat ng mga Heavy Equipment at Tunnel Boring Machine papuntang Ipo Dam )

Manageable CMC di Ravenna to inform two weeks prior to the schedule of transport the affected offices in particular with the local government offices, barangay and MWSS for them to have an ample time to prepare.

(Bigyan ng abiso ng CMC di Ravenna ang Lokal na Pamahalaan ng Norzagaray, Bulacan at MWSS dalawang linggo bago ang nakatakdang araw ng paglilipat ng mga heavy equipment at tunnel boring machine (TBM) para maisagawa ang kaukulang paghahanda)

Page 128: Updated Initial Environmental Examination

115

167. During the open forum at Brgy. San Mateo, the MWSS team was informed that the Barangay leadership is in transition with the election of Barangay Captain-elect Florencio SM. Abiol. Mr. Abiol inquired as to what benefits Barangay San Mateo will get from the on-going project. The team assured the incoming Barangay Captain that 250 households will have access to water supply initially.

168. The team also informed Mr. Abiol that upon his assumption to office on 30 June 2018, he becomes a regular member of the Multipartite Monitoring Team (MMT) and added that the Multipartite Monitoring Team (MMT) inspected the Tunnel on 3 May 2018.

169. The representative from the Local Government Unit Mr. Jaycee P. Capili requested the MWSS & CMC di Ravenna to coordinate the Traffic Management and Transportation Plan with the local government unit and other concerned authorities and to send representative to Brgy. Council Sessions to regularly update them on the progress of the project and address issues/concerns promptly.

Public Consultation at Barangay San Mateo, Norzagaray, Bulacan

Issues, Concerns, Interests from Stakeholders MWSS (and consultants, NWRB) Response

First, the representative from CMC di Ravenna informed the public that they will post updates

on the project at Brgy. Bigte Hall Bulletin Board.

Second, for concerns of Brgy. Bigte residents regarding AWTIP, the MWSS team requested

the Barangay Officials to inform the MWSS/CMC Project Team and the same will be relayed to

the Mayor and the contractor.

Third, the residents were informed that Brgy. Bigte will be served through the Bulacan Bulk

Water Supply Project (BBWSP) which has 388 MLD solely for Bulacan. The Water Treatment

Plant is located in San Jose Del Monte, Bulacan. The MWSS team requested that a survey of

the residents be conducted by the Local Government Unit and the Barangay Officials.

Fourth, the Barangay Council of Bigte adopted

Brgy. Resolution No. 2017-20 on 21 February

2017 requesting MWSS for raw water service

connection (“to tap”) for Sitio Settling, Brgy. Bigte, Norzagaray, Bulacan for drinking water,

cleaning, laundry, bathing and other domestic

use. This was endorsed by the Municipal

Mayor of Norzagaray, Bulacan on 31 May 2017

to MWSS. But the residents are one in saying

that it is more likely “they will die” from the unavailability of water for domestic use than

from the presence of coliform bacteria.

The Common Purpose Facility (CPF) pays

for conveyance fee, thus, it is prohibited to

tap for domestic use;

According to Rusty Romero of CMC, tests

conducted in the past indicate that raw

water from the area is not safe for

domestic use due to high presence of

coliform bacteria (pathogenic organisms of

fecal origin). It is prohibited to ensure that

water-borne diseases (drinking water

contamination) and other related health

Page 129: Updated Initial Environmental Examination

116

concerns will be avoided. If the residents

insist, they need to sign a waiver.

MWSS Deputy Administrator Leonor C.

Cleofas, CESO IV, Deputy Administrator

for Engineering and Operations wrote Hon.

Jovina A. LaMadrid, Barangay Chairman,

on 13 March 2017 stating therein that

MWSS with the assistance of the Common

Purpose Facility (CPF) will conduct the

field inspection to determine the possibility

of granting the request.

Fifth, residents from Sitio Settling complained

of muddy roads caused by the dump trucks

carrying wet spoils or waste materials from the

excavation of the tunnel boring machine.

The drainage project has been awarded to

the contractor by the DPWH and LGU

Sixth, the residents also complained of the drainage system in the area

The drainage project has been awarded to

the contractor by the DPWH and LGU

Seventh, the source of water for the residents of Sitio Settling is Balon (deep well/excavation) where they pay Php 300 per month to the owner. The water source is too small to meet the needs of the Sitio residents.

The residents asked MWSS if they could

tap at MWSS aqueduct even if this

necessitates the installation of water

meters and the designation of barangay

personnel as collectors for payment of

water consumption. The residents are of

the impression that the raw water is

cleaner than the water sourced from the

Balon.

One of the residents requested for MWSS

for the deployment of mobile water

treatment facility to address pressing

issues of drinking water contamination and

sanitation – to prevent water-borne

diseases and other related health

concerns.

Page 130: Updated Initial Environmental Examination

117

Picture of Public Consultation at Brgy. San Mateo, Norzagaray, Bulacan

Page 131: Updated Initial Environmental Examination

118

Picture of Public Consultation at Brgy. Bigte, Norzagaray, Bulacan

Page 132: Updated Initial Environmental Examination

119

Public Consultation with Indigenous Peoples (IPs) residing in Sitio Anginan/Pako/Santol, Sitio Sapang Munti, Sitio Ipo, Sitio Dyke, & other Ipo Communities from the Ipo Dam Area

170. IP Leaders headed by Mr. Ochie Aquino and Mr. Mario Cruz led the IP communities to the public

consultation conducted at the CPF covered parking area on 26 June 2018. The activity was undertaken in coordination with Ms. Regina Panlilio of the National Commission on Indigenous Peoples (NCIP) Bulacan Service Center.

After the Public Consultation with the IP communities, the MWSS team had a meeting with Ms. Regina Panlilio, Chief of the NCIP Bulacan Service Center to facilitate the Free and Prior Informed Consent (FPIC) Process. The 1st Community Assembly is scheduled on 13 July 2018.

7.3. Information Disclosure

171. Results of the surveys undertaken were discussed with Brgy. San Mateo, Brgy. Bigte and IP community at Sitio Ipo in Brgy. San Mateo. Public consultation meetings apart from the meetings held as reported in this IEE shall be conducted with the potentially affected communities in Brgy. Bigte and Brgy. San Mateo in the Municipality of Norzagaray. The meeting shall engage the stakeholders and discuss monitoring activities, implementation of the EMP that may require community collaboration, grievance redress mechanism as described in this IEE. Suitable communication method shall be used.

7.4. Additional Public Consultation and Information Campaign

172. To keep the directly impacted barangays aware of the progress of the project and necessary contribution, additional public consultations should be carried out after the detailed engineering design documents have been submitted by the CMC di Ravenna and approved by MWSS. Stakeholders must be invited and encouraged to participate in community discussions. The PMO-AWTIP, through its Consulting Firm, CMC di Ravenna and Concessionaires will be easily accessible to contact by the public on matters concerning project progress, adverse impacts, mitigation measures, environmental monitoring and grievances. The PMO, in coordination with the concerned Barangays of San Mateo and Bigte, will be responsible for organizing public consultations. Specifically, the conduct of the following:

a) At least one month prior to the start of construction mobilization, a joint social and environmental information campaign by the PMO-AWTIP, represented through its Consulting Firm, on the project’s social and environmental impacts with emphasis on health and safety concerns should be carried out to communities in Brgy. San Mateo and Brgy. Bigte;

b) During construction, informal interviews by the PMO-AWTIP together with the Consulting Firm to monitor environmental concerns of the same communities to be able to address them; and

c) During operation, in the first two years, periodic random interviews by the Concessionaires to continue to monitor the communities’ environmental concerns.

173. During entire project implementation, the final IEE and its EMP, as well as the GoP-approved EIS will be made available in the PMO and MWSS for the reading of the interested parties. Copies

Page 133: Updated Initial Environmental Examination

120

may be made available upon formal request.

7.5. Grievance Redressal Mechanism

174. Grievances raised on environmental impacts are critical to the health, wellness and safety of affected persons (APs). Hence, the proposed mechanism intends to be easily accessible and promptly responsive to APs’ environmental complaints. The proposed formal grievance redress mechanism (GRM) for the Project is presented below in Figure 22. It shows an integrated social and environmental mechanism. For environmental complaint, an AP may also opt for an informal approach to have his/her grievance addressed. The subsequent sub-section describes the approach for environmental complaint

7.5.1. Informal Approach

175. Informally, APs can lodge complaints directly to the CMC di Ravenna during construction or CPF (Common Purpose Facility) during operation. The CMC di Ravenna/CPF shall document and assess the complaint immediately. If assessment validates the complaint as within the scope of the GRM/eligible, the CMC di Ravenna/CPF shall act on the complaint within three days from receipt of complaint. If assessment invalidates the complaint (i.e., reveals the complaint as ineligible or not associated with the Project’s environmental performance), the CMC di Ravenna/CPF shall direct the AP to the Grievance Committee for confirmation, triggering the formal approach.

176. The Contractor/CPF shall report the following to the PMO-AWTIP within 2 days from receipt of complaint: (i) complaint received, eligible or ineligible, duly referenced; and (ii) actions to be taken/taken including timeline. The PMO-AWTIP shall obtain a written confirmation of satisfaction from the AP, 7 days from completion of resolution by Contractor/CPF.

7.5.2. Formal Approach

177. If complaint lodged informally is eligible but is not acted on within three days from receipt of complaint, or if AP is not satisfied with the resolution undertaken by the Contractor/CPF, he/she can access the formal approach. A Project Grievance Committee (GC) will be set up to consist of the Barangay Council (or IP Chieftain and Council for IP complaints), Contractor, CPF and MWSS as follows:

Step 1 Lodging a Complaint (Day 1) AP lodges complaint with the PMO-AWTIP or the Barangay.

Step 2 Documentation and Registration of Complaint (Day 1) PMO-AWTIP or Barangay registers lodged complaint and makes sure these are

duly referenced and provides AP with a copy of referenced complaint. The Barangay forwards a copy of the referenced complaint to the PMO -AWTIP.

Step 3 Screening (Day 1) PMO-AWTIP or Barangay screens if complaints relate to Tunnel 4. AP is informed if the grievance relates or does not relate to Tunnel 4. The Tunnel 4 Grievance Committee (GC) is also informed of the screening

result. If screening ruling is not acceptable to the AP, he/she may re-lodge his/her

complaint with the Grievance Committee, which will properly document the complaint.

Step 4 Complaint Investigation (Day 1-3) The GC conducts investigation of the complaint to determine if actions are

required or not.

Page 134: Updated Initial Environmental Examination

121

The AP is informed of the findings/ruling. If actions are required, AP is informed of the expected action timelines as set

out in the established mechanism. Agreement on actions and measures and time involved are made with the AP. Agreement is properly documented and filed. PMO-AWTIP, Barangay Council (or IP Chieftain and Council), Contractor/CPF and AP are furnished copies.

If actions are not required and GC ruling is not acceptable to the AP, AP may file the case with the Municipal Local Government Unit.

Step 5 Implementing the Agreed Action For minor action required: (Day 4-5)

The Contractor/CPF implements agreed on action within 2 days.

178. If AP is not satisfied with the completed action or if action is not started within 2 days from GC

ruling, AP may file case with the Municipal LGU. For major action required: (Day4/5-Day 8/9)

179. The Contractor/CPF provides agreed interim measure and starts work on the final action within 5 days from the GC ruling.

180. If AP is not satisfied with the completed action or if action is not started within 5 days from GC ruling, AP may file case with the Municipal LGU.

Step 6 Acceptance of Resolution (1 week after completion of action) If, according to the AP, the impact has been resolved satisfactorily, PMO-AWTIP

will obtain a written confirmation of satisfaction from the AP. This confirmation will signify closure of grievance and will form part of the grievance documentation. The GC, Barangay Council (or IP Chieftain and Council), Contractor/CPF and AP are furnished copies.

Step 7 Monitoring and Evaluation (for 1 week after completion of action) The PMO-AWTIP shall monitor the effectiveness of the resolution for at least a

week after completion of action. Monitoring and evaluation shall be properly documented and included in the

Environmental Monitoring Report (EMR).

181. The mechanism prescribes that the PMO-AWTIP shall inform the ADB of: complaints evaluated as major issues; and any appeal raised by dissatisfied AP.

182. The AP wishing to make a claim must first make an appeal to his respective barangay or to the IP leaders for the case of the Dumagats. The claim must be made in writing and should include brief details including factual background; issues; and AP’s position on the issue/s raised. The barangay must review the case within the context of existing policy, regulations, procedures and valid entitlement of the AP as provided in relevant implementing plans. The barangay council should respond within five days of receipt of the complaint. Should the grievance case cannot be resolved, the AP can file complain to the municipal level.

Page 135: Updated Initial Environmental Examination

122

Figure 22: Grievance Redress Mechanism Diagram

Page 136: Updated Initial Environmental Examination

123

VIII. Conclusions and Recommendations

183. The Project will improve and expand the raw water transmission system, increasing the reliability and security of raw water transmission and ensuring sustainable water supply services to Metro Manila.

184. The updated IEE concludes that most of the environmental impacts associated with the construction of Tunnel 4 are expected to arise during construction. Potential impacts will be localized and site-specific. Most of the identified impacts are low and temporary and if assessed carefully, it can be mitigated to an acceptable level without difficulty through good site, engineering and construction practices. No significant adverse impacts have been identified during operation phase.

185. The few impacts of high magnitude (without mitigation) during construction will not be distinct. Tunnel 4 will be the fourth tunnel to be constructed in the MWSS ROW. These impacts will not be sufficient to threaten the surrounding resources. During operation, low to moderate impacts will come from maintenance and repair.

186. The wildlife and river ecology surveys were done during the wet season. There is a need to assess the same parameters during the dry season, which is considered the base flow period to provide a more robust baseline data. The EMP should be updated whenever necessary.

187. More detailed infrastructure survey should be carried out and existing conditions of the infrastructure should be noted. At the preliminary stage of Tunnel 4 project, it was observed that there were poorly constructed housing units of the AFP subdivision. Such defects occurred prior to the tunnel construction and cannot be associated as an impact of the tunnel construction activity.

188. During the detailed design phase, further consultation is required to address the concerns raised during previous consultations to ensure that all public concerns are updated and publicly acknowledged and incorporated into detailed designs and updated EMP.

189. Also, during the detailed design, environmental due diligence should be conducted on the key associated facilities, namely: Ipo dam, Basin 3 and Aqueduct 5.

190. The EMP presented here should be updated during the detail design phase to:

Update the legislation and administrative arrangements,

Incorporate the results of further terrestrial and aquatic surveys, and land use surveys,

Update the impacts and mitigation presented herein,

Expand upon the mitigation and monitoring plans, and Develop capacity building needs.

191. In the event of design deviation, such as shift of alignment resulting in tunnel being located outside the MWSS ROW, change in inlet structure location and/or change in the method of construction, the MWSS through its PMO should immediately: (1) seek the advice of EMB Central Office if such design deviation warrants an ECC amendment; and (2) inform ADB should EMB advise for ECC amendment and finally, (2) seek ADB's clearance/concurrence for an IEE revision and/or EMP updating.

Page 137: Updated Initial Environmental Examination

124

192. The Contractor, CMC di Ravenna shall be required to prepare, implement and update, if necessary, the Construction Environmental Management and Monitoring Plan based on SPS compliant EMP. The following specific sub-management plans should form part of the CEMMP: chance finds recovery and removal; and include with the excavation sub plan placement of temporary berms and plastic sheeting between excavations and adjacent land, surface waters, and property to prevent erosion, sedimentation, or contamination from excavation work, noise control plan, dust control plan; and workers and staff health and safety plan.

193. Based on the above conclusion and recommendation, no further detailed EIA needs to be undertaken to comply with ADB SPS.

Page 138: Updated Initial Environmental Examination

125

PUBLIC CONSULTATION ATTENDANCE SHEET

Page 139: Updated Initial Environmental Examination

126

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 140: Updated Initial Environmental Examination

127

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 141: Updated Initial Environmental Examination

128

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 142: Updated Initial Environmental Examination

129

Page 143: Updated Initial Environmental Examination

130

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 144: Updated Initial Environmental Examination

131

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 145: Updated Initial Environmental Examination

132

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 146: Updated Initial Environmental Examination

133

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 147: Updated Initial Environmental Examination

134

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 148: Updated Initial Environmental Examination

135

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 149: Updated Initial Environmental Examination

136

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 150: Updated Initial Environmental Examination

137

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 151: Updated Initial Environmental Examination

138

BRGY. IPO WATERSHED, NORZAGARAY, BULACAN

Page 152: Updated Initial Environmental Examination

139

BRGY. SAN MATEO, NORZAGARAY, BULACAN

Page 153: Updated Initial Environmental Examination

140

BRGY. SAN MATEO, NORZAGARAY, BULACAN

Page 154: Updated Initial Environmental Examination

141

BRGY. SAN MATEO, NORZAGARAY, BULACAN

Page 155: Updated Initial Environmental Examination

142

BRGY. SAN MATEO, NORZAGARAY, BULACAN

Page 156: Updated Initial Environmental Examination

143

BRGY. SAN MATEO, NORZAGARAY, BULACAN

Page 157: Updated Initial Environmental Examination

144

BRGY. SAN MATEO, NORZAGARAY, BULACAN

Page 158: Updated Initial Environmental Examination

145

BRGY. SAN MATEO, NORZAGARAY, BULACAN

Page 159: Updated Initial Environmental Examination

146

BRGY. SAN MATEO, NORZAGARAY, BULACAN

Page 160: Updated Initial Environmental Examination

147

BRGY. BIGTE, NORZAGARAY, BULACAN

Page 161: Updated Initial Environmental Examination

148

BRGY. BIGTE, NORZAGARAY, BULACAN

Page 162: Updated Initial Environmental Examination

149

BRGY. BIGTE, NORZAGARAY, BULACAN

BRGY. BIGTE, NORZAGARAY, BULACAN

BRGY. BIGTE, NORZAGARAY, BULACAN

Page 163: Updated Initial Environmental Examination

150

Page 164: Updated Initial Environmental Examination

151

References

Alcala, A. C. 1986. Amphibians and Reptiles. Guide to Philippine Flora and Fauna. Volume X. Natural Resources Management Center and University of the Philippines, Manila.xiv+195 pp.

Alcala, A.C. and W.C. Brown. 1998. Philippine amphibians: An illustrated field guide. Book Mark, Inc. Makati City, Philippines.

Alcala, A.C., A.C. Diesmos, L.C. Afuang, J.C.T. Gonzalez and C.B. Banks. 1999. Proposed inclusions of Philippine amphibians in IUCN, Red List and Philippine National List. Unpublished.

Alcala-Breva, L. 2006. Carbon Stocks Assessment of a Mangrove Forest in Padre Burgos, Quezon, Philippines. MSc Thesis. University of the Philippines. Los Banos, Laguna.

Banaticla, R., R. Sales and R. Lasco. 2003. Biomass Equations for Tropical Tree Species Using Secondary Data from the Philippines. ACIAR Carbon Sequestration Study. Environmental Forestry Program, UPLB College of Forestry and Natural Resources. College, Laguna.

Brady, NC. 1974. The Nature and Properties of Soils. 8th Edition. Macmillan Publishing Co. Inc. New York.

Castillo, JA. 2004. Diversity Assessment and Numerical Classification of the Natural Forest of the Los Banos Experiment Station, Luzon Island. MSc Thesis. University of the Philippines. Los Banos, Laguna.

Collar, N.J., N.A.D. Mallari and B.R. Tabaranza, Jr. 1999. Threatened birds of the Philippines: The Haribon Foundation/Bird Life International Red Data Book. Department of Environment and Natural Resources (DENR) and Environment Agency of Japan. Makati City: Bookmark.

Crombie, R. Distribution by island of herps in the Philippines. Draft Copy.

DAO 2016-08. Water Quality Guidelines and General Effluent Standards of 2016

DAO 1992-16. Addendum to DAO 42 which provides the Regulations and Guidelines Governing the Establishment and Development of IFPs

DAO 1992-25. NIPAS Implementing Rules and Regulations

DAO 1994- 26A. Philippine Standards for Drinking Water

DAO 2000-21. Revised Guidelines In The Issuance Of Private Land TimberPermit/Special Private Land Timber Permit (PLTP/SPLTP).

DAO 2000-81. Implementing rules andregulations for RA 8749 (Philippine Clean Air Act)

DAO 2003-30. Implementing Rules and Regulations (IRR) for the Philippine Environmental Impact Statement (EIS) System

DAO 2004 – 52. Revised Guidelines in the Issuance of Cutting/Harvesting Permits inPrivate titled lands.

DAO 2007-17. Rules and Regulations governing Special uses within protected areas

DAO 2008-26. Revised Implementing Rules and Regulations of Republic Act No. 7586 or the National Integrated Protected Areas System (NIPAS) Act of 1992

De Guzman, ED, RM Umali and ED Sotalbo. 1986. Guide to Flora and Fauna: Dipterocarps and Non-Dipterocarps. Volume III. Quezon City: Natural Resources Management Center, Ministry of Natural Resources and University of the Philippines.

DENR MO 2011-04 Strict Regulation of activities, projects and land uses in all areas proposed for inclusion in the National Integrated Protected Areas System (NIPAS)

DENR EMB. EIA DRR/CCA Technical Guidelines. November 2011

Page 165: Updated Initial Environmental Examination

152

Dickinson, E.C., R.S. Kennedy and K.C. Parkes. 1991. The birds of the Philippines. B.O.U. Checklist No. 12. British Ornithologists’ union, Cambridge, United Kingdom.

EO #23

Fernando, E.S. and ML Castillo. 1996. Field Checklist of Species in FBS 21 (Taxonomy of Forest Plants). Third Edition. Department of Forest Biological Sciences, University of the Philippines Los Baños. 18 pp.

Fernando, ES. 1998. Forest formations and Flora of the Philippines: Handout in FBS 21. College of Forestry and Natural Resources (unpublished).

Gonzalez, J.C.T. 1996. State of the art report on reptiles of the Philippines. A paper presented during the Wildlife Conservation Society Symposium and Workshop. University of the Philippines, Diliman, Quezon City, Philippines. Unpublished Report.

Heaney, L.R., D.S. Balete, M.L. Dolar, A.C. Alcala, A.T.L. Dans, P.C. Gonzales, N.R. Ingle, M.V. Lepiten, W.L.R. Oliver, P.S. Ong, E.A. Rickart, B.R. Tabaranza and R.C.B. Utzurumm. 1998. A synopsis of the mammalian fauna of the Philippine Islands. Fieldiana. No. 88 (1493). 61 pp.

Hilton-Taylor, C. (Compiler) 2004. 2004 IUCN Red List of Threatened Species. IUCN, Gland, Switzerland and Cambridge, UK.

Hoanh and Natividad. 1987. Soil Sampling Techniques for Forest Plantation and Agroforestry Development. Ecosystems Research and Development Bureau. College, Laguna.

Kent, M andCoker, P. 1992. Vegetation Description and Analysis: A Practical Approach. CRC Press, Boca Raton, Ann Arbor and Belhaven Press, London. 333 pp.

Madulid DA. 2000. A Pictorial Cyclopedia of Philippine Ornamental Plants. 2nd edition. Bookmark, Makati City. 389 pp.

Madulid DA. 2001. A Dictionary of Philippine plant names. Volume II. Bookmark, Makati City. 329 pp.

Mallari, N.A.D. and A. Jensen, 1993. Biological diversity in the Northern Sierra Madre, Philippines: its implication for conservation and management. Asia Life Sciences. Vol. 2. No. 2. pp. 101

Martin-Prevel, P., J. Gagnard and P. Gartlier. 1984. Plant analysis as a guide to the nutrient requirements of temperate and tropical crops. La Voisier Pub. Inc. NY, USA.

Mittermeier, R. A., N. Myers, and C.G. Mittermeier. 1999. Hotspots, Earth's Biologically Richest and Most Endangered Terrestrial Ecoregions. CEMEX, Mexico City. 431 pp.

Mittermeier, R. A., P. Robles Gil and C.G. Mittermeier. 1997. Megadiversity, Earth's Biologically Wealthiest Nations. CEMEX, Monterrey, Mexico. 501 pp.

Moody, K, CE Munroe, RT Lubigan and EC Paller, Jr. 1984. Major Weeds of the Philippines. College, Laguna: Weed Science Society of the Philippines and University of the Philippines Los Baños.

Odum, E. 1971. Fundamentals of Ecology. 3rd edition. London Press.

Ong, PS., LE Afuang, and RG Rosell-Ambal (eds.) 2002. Philippine Biodiversity Conservation Priorities: A Second Iteration of the National Biodiversity Strategy and Action Plan. Department of Environment and Natural Resources-Protected Areas and Wildlife Bureau, Conservation International Philippines, Biodiversity Conservation Program-University of the Philippines Center for Integrative and Development Studies, and Foundation for the Philippine Environment, Quezon City, Philippines

PAWB Technical Bulletin #2013-01 (list of Protected Areas under the National Integrated Protected Areas System (NIPAS)

PCARRD 1994. The Mango Technical Committee. The Philippines Recommends for Mango. Los Banos, Laguna: PCARRD and PARRFI, 1994. 124p – (PCARRD Philippines Recommends Ser. No. 38-A/1994).

PAGASA – DOST. Climate Change in the Philippines. February 2011.

Page 166: Updated Initial Environmental Examination

153

PCARRD 2006. The Committee on Soil Fertility Management. Philippines Recommends for Soil Fertility Management. Los Banos, Laguna: PCARRD-DOST, 2006. 201p. – (Philippines Recommends Series No. 36-D).

PD 705 as amended by EO 277. Revised Forestry Code of the Philippines

PD 953. Requiring the planting of trees in certain places and penalizing unauthorized cutting, destruction, damaging and injuring of certain trees, plants and vegetation

PD 984. Providing for the revision of republic act no. 3931, commonly known as the Pollution Control Law, and for other purposes

RA 7161. An act incorporating certain sections of the national internal revenue code of 1977, as amended, to presidential decree no. 705, as amended, otherwise known as the "revised forestry code of the Philippines", and providing amendments thereto by increasing the forest charges on timber and other forest products.

RA 7586 an act providing for the establishment and management of National Integrated Protected Areas System, defining its scope and coverage, and for other purposes

RA 8749 Philippine Clean Air Act

RA 9275 Philippine Clean Water Act

Racelis, E. 2000. Carbon Stock Assessment of Mahogany and Dipterocarp Plantations in Mt. Makiling Forest Reserve. MSc Thesis. University of the Philippines. Los Banos, Laguna.

Rojo, JP. 1999. Revised Lexicon of Philippine Trees. Forest Products Research and Development Institute. College, Laguna. 484 pp.

Tabaranza, B.R. and N.A.D. Mallari. 1997. Birds. Pp. 99-136. In the Philippine Red Data Book. Wildlife Conservation Society of the Philippines. Bookmark, Inc., Makati, Philippines

Thompson, L.M. and F.R. Troeh 1978. Soils and Soil fertility. 4th edition. McGraw-Hill Book Co. NY. 516 p.

UPLB Soil Test Kit Manual (undated). Soil Analysis and Fertilizer Usage. Department of Soil Science, College of Agriculture, UPLB, College, Laguna.

Bermuda, J. 1995. Vegetation Analysis of the Tree Layer of Lowland Dipterocarp Forest at Quezon National Park, Quezon Province, Philippines. MSc Thesis. University of the Philippines. Los Banos, Laguna.