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8/10/2019 Hara, Takeuchi, Palijon & Murakami 2008 Landfill Development in the Urban Fringe of NCR
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Landfill development in the urban fringe of Metro ManilaAuthor(s): Yuji Hara, Kazuhiko Takeuchi, Armando M. Palijon and Akinobu MurakamiSource: GeoJournal, Vol. 71, No. 2/3 (2008), pp. 127-141Published by: SpringerStable URL: http://www.jstor.org/stable/41148246 .
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8/10/2019 Hara, Takeuchi, Palijon & Murakami 2008 Landfill Development in the Urban Fringe of NCR
http://slidepdf.com/reader/full/hara-takeuchi-palijon-murakami-2008-landfill-development-in-the-urban-fringe 2/16
GeoJournal
2008)
71:127-141
DOI
10.1007/S10708-008-9150-Z
Landfill
evelopment
n
the urban
fringe
f
Metro Manila
Yuji
Hara
*
Kazuhiko Takeuchi Armando
M
Palijon
*
AkinobuMurakami
Published nline: 20
May
2008
©
Springer
cience+BusinessMedia B.V. 2008
Abstract
In
low-lying
reasof urban
nd suburban
regions
n
Asia,
theuse
of andfill as allowedurban
landuse to encroach nto
watery
andforms,
uch s
back
marshes,
which were
formerly
sed as rice
fields.
o
improve
nderstanding
f the ssociations
between
and-use
atterns
nd andfill
evelopment,
we carried ut a case
study
n
the urban
fringe
f
Metro
Manila in the
Philippines.
We examined
landfill
olumederived
rom and-use
hangeusing
GIS,
and
field
urveyed
ualitative spects
of the
landfillsed.We calculatedhe ate fapplicationf
Y. Hará
(IS1)
Transdisciplinary
nitiative orGlobal
Sustainability
(TIGS),
Integrated
esearch
System
or
ustainability
Science
(IR3S),
The
University
f
Tokyo, Hongo
7-3-1,
Bunkyo-ku,
okyo
113-8654,
Japan
e-mail:
K. Takeuchi
Laboratory
f
Landscape Ecology
and
Planning,
Department
f
Ecosystem
tudies,
Graduate chool of
Agricultural
nd Life
Sciences,
The
University
f
Tokyo,
Yayoi
1-1-1,
Bunkyo-ku, okyo
113-8657,
Japan
A. M. Palijon
College
of
Forestry
nd
Natural
Resources,
University
f
the
Philippines
os
Baños,
College, Laguna
4031,
Philippines
A. Murakami
Department
f Social
Systems
nd
Management,
Graduate chool of
Systems
nd nformation
ngineering,
University
f
Tsukuba,
Tennodai
1-1-1,
Tsukuba
Science
City,
baraki
305-8573,
Japan
landfill
n
ow-lying
ousing
evelopment
reas o be
5.0
x
103
m3km 2
year 1,
most f which onsisted
of offsite
isposal
of construction aste or crushed
rock
produced y
urban
evelopment
nd
renewal
n
the
djoining plands.
heflow f
fill
material rom
offsite
ources o onsite andfill
evelopment
reas
was
on the basis of individual
greements
etween
suppliers
nd
developers.
Keywords
Landfill Land use
•
Landform
Material low MetroManila
Introduction
The
space
occupied
by
human
wellings hroughout
theworldhas been
expanding
ith he ssistance f
technologicaldevelopments
n civil
engineering
(Hooke 2000).
The introductionf
large-scale
on-
struction
equipment,
such as excavators and
bulldozers,
as made it
possible
to transformand-
forms hatwere
previously
onsideredo be unusable
as
living pace
Hooke
1999;
Kiersch
001). Quarries
(Mouflis 008),
aggregatemining
Drew 2002),
cut-
and-fill perations or urban and developmentn
hilly
areas
(Tamura
nd Takeuchi
1980),
and
land
reclamation n
coastal
regions
Hooimeijer
et al.
2005)
are common
xamples
f such
anthropogenic
landformransformation.
hese transformationsre
expected
o occurmore
ntensively
n
regions
acing
rapid population
rowth
Rivas
et al.
2006),
espe-
cially
in
Asia,
where vast
populations
re
being
Ô
Springer
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8/10/2019 Hara, Takeuchi, Palijon & Murakami 2008 Landfill Development in the Urban Fringe of NCR
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8/10/2019 Hara, Takeuchi, Palijon & Murakami 2008 Landfill Development in the Urban Fringe of NCR
http://slidepdf.com/reader/full/hara-takeuchi-palijon-murakami-2008-landfill-development-in-the-urban-fringe 4/16
GeoJournal
2008)
71:127-141
129
Fig.
1 Location
map.
Photo
a)
was taken ver
aranaque
ity
irected orthoward heMakati
entral usiness istrictn the
upland
andform.hoto
b)
shows
ypical
eaturesf
ow-lying
rea n
TaguigCity;
rom ortho south
Data
sources
nd
analytical
methods
We conducted ield
urveys
or
total
of
approxi-
mately
wo months etween
2001
and
2005,
and
collected ata as shown
n Table 1. In the
field,
we
verified
and-use
nterpretations
f aerial
imagery,
intervieweddministrativefficersnd ocal
workers,
recorded
ill
materials,
nd took andform easure-
ments.
Geographic
Information
ystem
(GIS)
technologyTNTmips
ersion
.0,
Microimages
ne,
Lincoln,NE, USA;
ArcGIS version
.0, ESRI,
Red-
lands, CA, USA;
VectorWorksversion
11.5,
Nemetschek orthAmerica, olumbia,MD, USA)
was usedfor ata
digitization,patial nalyses,
nd he
drawing
f
figures.
Preparation
f
digital
and-use
maps
We used n
existing
986
:10,000-scale
and-use
map
in
digital
ector ormats a base
map
for ur and-use
investigation
nd
ntegrated
and-use
ategories
herein
to create 5classes f anduse
Fig.
2).
Using
his s a
base
map,digital
and-use
maps
n
vector ormat or
1 66 nd 004were
roduced y
visual
nterpretation
f
aerial
photographs
nd satellite
magery.
We
scanned
the
966
erial
hotographs
t600
dpi
resolution,
dded
georeference
ata,
nd
ompiled
rastermosaic
mage
to
produce
he
1966
and-use
map.
QuickBird
atellite
imagery
as used to
produce
he
2004 land-use
map.
Theboundariesfour15
and-use lasses or
966
nd
2004 were
digitized y
means of
on-screenmanual
interpretation.
e
used 1961
opographic ap,
1966
land-usemap, nd 2001digital rthophotoosaic o
support
ur
nterpretation,
nd
also verifiedur nter-
preted
and
uses
by
nterviewing
ocal residents.
Measuring hanges
n land elevation
The
1966
and
1986
l:10,000-scale
opographic
aps,
which
rovided
levations ccurate o
within
0
cm,
â
Springer
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8/10/2019 Hara, Takeuchi, Palijon & Murakami 2008 Landfill Development in the Urban Fringe of NCR
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130
GeoJournal
2008)
71:127-141
Table
1 Data sources
Year
Scale
Format
Publisher
Aerial hotographs 1966 1:10,000 Paper rint NationalMappingndResourcenformation
(gray
cale)
AuthorityPhilippines)
2001
1:10,000
Digital
mage Geo-Surveys Mapping
nc.
Philippines)
(gray
cale)
Satellite
magery
2004
2.44
m
Multi-spectral
ensor
DigitalGlobe
nc.
(QuickBird)
resolution
image
Topographic
aps
1961
1:50,000
Paper
National
Mapping
ndResourcenformation
Authority
1966
1:10,000
Paper
National
Mapping
ndResourcenformation
Authority
1986
1:10,000
Paper
Japan
nternational
ooperation
gency
Land-use
maps
1966
1:25,000
Paper
National
Mapping
ndResourcenformation
Authority
1986
1:10,000
Digital
ector
ormat
Japan
nternational
ooperation gency
Landformlassification 2002 1:10,000 Digital ectorormat Hara t al. (2002)
map
Geologicmaps
1980s-
1:50,000
Paper
Mines ndGeosciences ureau
Philippines)
Present
2004
1:2,000,000
Digital
ector ormat
Geological
urvey
f
Japan
Fig.
2 Land-use
maps
or
966,
986,
nd
2004
and
landformlassification
ap
Hara
t
al.
2002).
The
square
n
the andform
classification
ap orresponds
othe reaof
Fig.
5
wereused
to
measure
hanges
n land elevation.
We
firstcanned
hese
maps
t 300
dpi
resolutionver ur
entire
tudy
rea and
added ocation
nformation. e
Ô
Springer
then
igitized
nd
extracted
he levation
oints
rom
the1986
map.
By comparing
he
wo
ets
felevation
data,
we obtained
he
hanges
n levation rom 66
to
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8/10/2019 Hara, Takeuchi, Palijon & Murakami 2008 Landfill Development in the Urban Fringe of NCR
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GeoJournal
2008)
71:127-141
131
1986
at 50-cm
ncrements.hese
were
xpressed
s
610
digital
ector
oints
within
he
tudy
rea.
Quantifyinghevolume f andfill evelopment
By
overlaying
he
previously
etermined
levation
change
ata
points
n
the
1966
and 1986
digital
and-
use
maps,
we extracted
hose
oints
hat ad
changed
from ural o urbananduse
residential
se,
business
use,
factory,
acant
and,
nd
road)
between 966
and
1986.
These
points
were then
grouped
ccording
o
landform
ype except pland)
yoverlaying
hem n
the
digital
andformlassification
ap
of
Hara et al.
(2002).
Next,
he
points
within ach
landform
ype
were classified
nto and-use lasses
by
overlaying
them n the1986 and-use
map.
We then
raphed
he
relationshipetween levation hange nd land use
by
andform
ype.
To evaluate
the volume
of
landfill,
we first
compared
he land-use
maps
for
1966, 1986,
and
2004 to determine
hich reas
had
changed
from
rural o urban
and use between
966 and
1986,
and
between1986
and
2004.
We then
compared
hese
areas
with the
landform lassification
map
and
calculated
he rea
of
rural-to-urban
and-use
hange
for ach andform
ype. y multiplying
hese reas
of
land-use
hange
by
the
average
elevation
hanges
within hose
areas,
we calculatedthe
volume of
landfilling
or ach
andform
ype.
Recording
andfillmaterials nd
measuring
transect
eatures
To
support
he
andfill
olume-landform
ype-land
use
interrelationships
erived
rom urGIS
analyses,
we undertook
ield
urveys
f
development
ites
n
the southern
art
f the
study
rea where ntensive
land
development
s
taking lace.
We recorded
he
characteristics
texture
nd
color)
of
fill
materials,
the
height
f
thefill
profile,
ndthe
ayering
ithin
the
fill
profile.
Where
possible,
we also
interviewed
site
managers,
orkers,
evelopers,
nd landowners
to find utwhat illmaterialshey se,why hey se
them,
nd their ource
nd cost.
Initially,
he 1966
and
1986
l:10,000-scale
opo-
graphicmaps
were
ompared
o elect
representative
transect
ver which
to measure
fill
profile.
o
supplement
ur
nterpretation
f he1966
topographic
mapalong
he elected
ransect,
e
then nterviewed
local
government
fficials
nd
ong-term
esidents
nd
took nto ccount
he nformation
leaned
romhem o
determine
n
original
966
base ine f he and urface
alongthe transect.We recorded and use alongthe
transectnd useda hand evel and laser
rangefinder
400LH
(Opti-Logic Corporation,
ullahoma,TN,
USA)
to takefieldmeasurementsf
the urrentand-
surface
rofile.
We interviewed
esidents
long
the
transect
o find ut when
and
how
they
made
their
housing
oundations,
hat illmaterials
hey
sed,
nd
where hesematerials
ame from.
n
some
cases,
we
were llowed nto
roperties
ndwere
ble
o heck he
fillmaterials t
the
plot boundary.
o determinehe
timing
nd method f constructionf
public
oads n
the
ransect,
e visited he
ivil
ngineering
ivision t
thePateros
Municipal
ffice nd
used
records froad
constructionork.
Tracing
heflow f
andfill
materials
Because
of a lack of
government
ecords n land
development
n Metro
Manila,
we
mainly
sed field
interviewso obtain
hedata we
needed
o trace he
flowof landfillmaterials or and
preparation.
ur
interviewswere started
t the
development
ites
wherewe recorded
hefillmaterials
n
use. Extensive
interviews ere undertaken
ith ocal contractors
and
pit
owners on matters uch
as the
price
of
materials,
he
supply-demand
alance,
nd
govern-
ment egulationselated o andfillmaterials. e also
conducted
nterviews nd collecteddata about
the
flow
of landfillmaterials
t the Mines and Geo-
sciences
Bureau
(MGB)
of the
Department
f
Environment
nd Natural
Resources
(DENR)
in
Manila,
t
the
MetroManila
Development
uthority
(MMDA),
and with he ivil
engineering
ivisions
f
the
Taguig
and Pateros
Municipalities.
Results
Land-use
hanges
nd andform
ypes
Land-use
maps
for
966, 1986,
nd
2004,
as
well as a
landformlassification
ap,
are shown
n
Fig.
2. In
1966,
most of the
developed
areas,
including
he
business
district,
eresituated n the northwestern
uplands
f the
tudy
rea,
nd factories ere ocated
on
back
marsh andforms
long
heriver.Within
he
4y
Springer
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8/10/2019 Hara, Takeuchi, Palijon & Murakami 2008 Landfill Development in the Urban Fringe of NCR
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132
GeoJournal
2008)
71:127-141
low-lying
reas,
most f theresidential
evelopment
was
along
natural
evees,
showing
that
land-use
patterns
ad
adapted
o thenaturalocal environment.
By 1986,clearing fforestsnd speculative evel-
opment
fvacant andhad ed to
extensive esidential
and business
development
n the
northwestern
uplands.
n
low-lying
reas,
and
development
as
mainly
n the
backmarshes ehind henaturalevees.
By
2004,
the southwestern
pland
rea was
largely
convertedoresidentialand
use,
mainly hrough
he
development
f
arge
residentialubdivisions.
n
the
low-lying
reas,
residentialand use and
factories
were
beginning
o fill the
areas
between
natural
levees.
Thus,
n
the
study
rea between1966 and
2004,
land-usehad been transformedrom
atterns
adapted
to the natural nvironmento a
diverse
pattern
hat ad
overcome he
estrictions
mposed
y
thenatural
andforms.
Interrelationsmong andfill,andforms,
and and
use
Figure
shows the
interrelations
mong
landfill,
landforms,
nd land use. About
half of
the total
urbanizedandhas been
developed y
using
ill n
all
landform
ypes,
nd the
peak
of fill
hicknesss
1
m.
The
maximum ill
hickness
or esidential
evelop-
ments n the
natural evee
landform
s about 1
m,
whereas
hat
n
areas
of
acustrine
lains
s
less
than
50 cm.
Figure
shows stimates f
he
umulative
rowth
of fill olumenthe
tudy
rea. The
greatest
ncrease
Fig.
3
Landfill,andform,
and anduse
interrelationships
Ö
Springer
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GeoJoumal
2008)
71:127-141
133
Fig.
4
Cumulative
rowth
n the
volume of
landfill
y
landform
ype
in the use of filloccurred n the lower acustrine
terrace andform. etween
1966
and
2004,
the
volume of fill
applied
to landform
ransformation
almost oubled n the tudy rea.
Characteristics
f
andfillmaterials
anda
representative
ectional
rofile
Figure
and Table2 showthecharacteristicsf the
materials
sedfor andfills
observed
uring
urfield
surveys.Many development
ites
use construction
waste such as broken oncrete or andfill. ocal
contractorslso sell crushed
ock,
ncluding
local
product
nown s
adobe,
nd ahar
eposits,
hich s
composed
of
volcaniclasticmaterialfrom round
Mt.
Pinatubo,
lso
commonly
alled
white and
n
Metro Manila. At several
sites,
we
found that
landowners llowed the
dumping
f construction
waste nplots hat heyntend odevelop nthenear
future. t some
sites,
andowners
ccepted
umping
of
construction aste for andfill
or
payment y
truck rivers f around 0
pesos per
truckload,
nd
also asked the truckdrivers o level the land in
preparation
or
onstruction.
herefore,
t
a consid-
erablenumber f
development
ites,
he fill
onsists
of
mixed
materials,
ncluding
mainly
broken on-
crete,
ut lso adobe and other
olidwaste.We found
that ahar
s
used
mainly
o make hollowconcrete
blocks orwall
construction,
ndcrushed ock sused
mainly
n
asphalt
or
pavement
nd
driveways.
The sectional
rofileFig.
6)
shows,
romwest o
east,a characteristicattern f fillalong a typical
sequence
f
ow-lying
andform
nits: atural
tream,
natural evee
(originally
nhabited),
ower
acustrine
terrace,
atural
evee
(originally
nhabited),
nd the
former iver ourse.Fill has sometimes een
used
under raditionalaised-floorouses on the natural
levees.
n
some old
houses,
andowners ave
placed
fillmaterial
mainly
ocal
clay
and
laterite)
nto he
traditionallypen-air round
loor f their
houses,
which
s sometimes ater enclosed to add to their
living
space.
Some
landowners
have
added
fill
several times
over the
past
three
decades,
often
Fig.
5
Map
and
photographs
f landfill bservationites.
Table 2
provides
etails f material bserved
t
numbered
sites.
hotographs
how
ypical
andfillmaterials:ahar nd
crushed
ock
t a
contractor's
hop top
eft),
roken
oncrete
fill
top right),
dobe
fill
bottomeft),
nd ocal
clay being
used
n
road onstruction
bottom
ight).
ection
rofile
-B is
shown n
Fig.
6
Ö
Springer
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GeoJournal
2008)
71:127-141
Table
2 Material
urvey
ist
Site
Development
Transformation
ainmaterial
Price
pesos/m3)
number
ite or
type Type TextureColor Crushed Sand LateriteBroken
rock
concrete
0 Residential
se
Landfill
Broken oncrete G
- - - - -
1 Governmental
all
Landfill Broken oncrete G
- - -
2 Residential
se Landfill
Broken oncrete
G
- - -
3
Fill ontractor's
hop
-
Lahar S 5Y5/1 500 500 500
4 Fill ontractor's
hop
-
Crushed ock G 5B3/1
675
430
-
90
5
Fill
ontractor's
hop
-
Lahar
S 5Y5/1 550 550
-
6
Road
Landfill
Local
clay
HC 2.5Y3/3
- -
7
Road
Landfill
Lahar S 5Y5/1
- -
8
Residentialse Cut
Crushedock
Adobe)
G 7.5YR3/1
- -
9
Fill ontractor's
hop
-
Lahar
S 5Y5/1 500 450
-
100
10 Residentialse Landfill LocalClay
HC 2.5Y3/3
- -
11 Residential
se
Landfill Crushed
ock
Adobe)
G 7.5YR5/4
- -
12 Residentialse
Landfill
Broken oncrete
G
- -
13 Fill ontractor's
hop
-
Lahar S 5Y5/1 500 500
-
14 Residential
se Landfill
Laterite
LiC 7.5YR4/3
- -
15
Residentialse Landfill
Broken
oncrete G
- - -
16
Residentialse
Landfill
Laterite LiC 7.5YR4/3
- -
17 Residentialse
Landfill Crushed
ock
Adobe)
G 7.5YR5/4
- -
18
Residential
se
Landfill
Broken oncrete G
- -
-
19 Residential
se
Landfill
Crushedock
Adobe)
G 7.5YR5/4
- -
20
Residentialse
Landfill Broken oncrete G
- -
-
during
enovation
f their
houses. New houses
are
commonly uilt on higher oundationshan tradi-
tional ouses.
. Rosales
Street,
t thewestern nd
of
our
profile,
ollows he
natural evee.
According
o
the ivil
engineering
ivision
f thePaterosMunici-
pal
Office,
t wasnot
paved
until
998,
when50 cm
of
fill
was
applied
at a cost of
approximately
00
pesos per
cubic meter.
Moving
ast fromhenatural
levee to the ower
acustrine
errace,
he and surface
becomes
gradually
ower,
nd
temporary
nd
slum
housing
onstructed
f
concrete ollow
blocks with
galvanized
ron
oofing
n fill f
clay
and construc-
tionwaste
begins
o dominate.
or houses
builthere
in
the
1980s,
wners
ut
dditional
ill
n
the
ground
floors fternitial onstruction,n some cases result-
ing
in the need to
cut the bottom
ff
ground
loor
doors.
Nevertheless,
he evel
of he
pathways
n front
of the houses
has
remained,
n
average,
around
40
cm
higher
han he
ground
loor f theirhouses
becauseof
regular
ddition f fill o the
pathways
y
the local
community.
n thecenter f the
profile,
Ö
Springer
between he natural
evees,
abandonedrice fields
have become wampy acant and.Theswampyand
has become
unsanitary
ecause of
poor
drainage
nd
dumping
f solidwaste. ast of the
wampy
rea,
he
land
gradually
ises
and
temporary
ousing
n
clay
fill
ontinues ntil henext
naturalevee
s
reached.
Flow of fillmaterial
Figure
shows he
geology
nd source reas for
fill
materials or he MetroManila
region.
n the ow-
lying evelopment
iteswithin he
tudy
rea,
ahar
s
almost
exclusively
sed
in
concrete,
nd
to make
hollow
oncrete locks n
particular.
t is sometimes
also used for he base of majorroads. The lahar s
trucked rom n area at thefoot f Mt. Pinatubo
n
Pampanga
rovince
Fig.
7).
The
cost
o the nduser
in our
study
rea s about
6,000
pesos per
truckload,
which s
equivalent
o about
500
pesos per
cubic
meter. t the
ource,
t
costs600
pesos per
ruckload,
equivalent
o
50
pesos per
cubicmeter.
ccording
o
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GeoJoumal
2008)
71:127-141
135
Fig.
6 Sectional
profile
A-B.
Photographs
how
examples
of
typical
urrentand use and landfill
long
the transect.
rom
left oright:modifiedraditional aised-floor ouse on a natural
levee,
slum
housing
onstructed
f concrete ollow blocks and
galvanized
ron
roofing, welling
where
regular
ddition f
fill
has necessitated
utting
ff the
bottom of
a
door,
swampy
abandonedpaddyfield, egetablepatch, emporary ousing n
clay
fill,
nd a
path slopingup
to
the
main road
our interviews
t the source
pits,
factories,
nd
control
oints
n the
source
area,
production
as
more
than
1,300
truckloads
er
day,
equivalent
o
1.8
x
104
m3
per
day, during
he
peak period
of
reconstruction
fter he xtensive
amage
aused
by
the
1991
eruption
f
Mt. Pinatubo. he lanarfrom
Pampanga
rovince s used for constructions far
away
as
Batangas
Province,
pproximately
00
km
south f Metro
Manila. Before he
1991
eruption
f
Mt.
Pinatubo,
iver
and
was
commerciallyxploited
for use as a construction
aterial.The
eruption
depositedargevolumes f lahar near thevolcano,
and local landowners oon
began
to use
private
contractorso remove he aharfrom
heir
and. The
contractors
ay
an excavation ee to landowners. n
organizationomprising
he
private
ontractorsnd
construction
ompanies
et
up
control
oints
t
the
entrance o the source area
to monitor xcavation
practices.
he
organization
ays
a fee to the ocal
government
n the basis of the number f
trucks
passing hrough.
Crushed rock
is used
for
surface
filling
nd
leveling.
t is trucked
mainly
rom an Mateo
and
TayTay
in
Rizal Province
Fig.
7),
a
hilly
and
mountainous
rea
east
of
our
study
rea. The cost
to the end
user
of this
rushed
ock
s about
7,000
pesos per
truck,
quivalent
o
580
pesos per
cubic
meter. different
ype
f crushed
ock,
ocally
alled
adobe,
s used
mainly
or andfill. his
is
produced
from heuplands rea Fig.7), especiallynthe rea
of
Makati
City (Fig.
1),
through
urface
eveling
work or
arge-scale
hopping
enters r subdivision
developments.
n the
uplands
rea,
the Pleistocene
Guadalupe
ormation
largely
olcanic
uff)
utcrops
at the urface
Aurelio
ndPeña
2002).
Leveling,
nd
in
some areas
cutting,
f theuneven nd
rocky
and
Ô
Springer
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136
GeoJournal
2008)
71:127-141
Fig.
7
Regionalmap howing
ources f
fillmaterial.hoto
a)
shows
ahar
mining
t
Pampanga.
hoto
b)
shows ock
mining
t
TayTay
surface
for new
land
development rovides
arge
volumes
f adobe.
They
re trucked
irectly
o low-
lying
onstruction
ites,
r
to contractor
hops
nthe
low-lying
reas,
where t s
mixedwith onstruction
waste
nd sold for
bout
1,200
pesos per
truckload,
equivalent
o about 100
pesos
per
cubic meter. fter
leveling
r
cutting
t
upland
onstruction
ites,
high
quality
ahar nd crushed
ock are used
for urface
filling
o
provide
oundations
o
support
arge
and
heavybuildings.
Construction
aste
n theform f
broken oncrete
is
themain
fillmaterial sed
for
ow-lying evelop-
ment ites.
t
s
produced
mainly
rom he
upland
rea
as
a result f
building
enovation
ork,
nd s
mixed
with dobe and trucked
o
development
ites
n
low-
lying
reas. Demolition
f old concrete
overnment
buildings
n
low-lying
reas
provides
additional
concretewastefor
fill
t
nearby evelopment
ites.
This
waste is
often
dumped,
with
permission
f
landowners,
nto acant
lots
or
se
as
fill
or
uture
land
developments.
therwise
t s
provided
o local
contractor
hops
for ale.
Local peoplethatwe interviewednAugust 005
along
the transectA-B
in
Fig.
5 said
that
they
previously
sed fill
composed
of
clay
and latente
from
ntipoloFig.
7),
thenearest
illy egion
ast
of
our
study
rea. An
82-year-old
omanwho was a
long-time
esident
aid that
hey
used
to
regularly
collect these
materials
nd
carry
them
by
two-
Ô
Springer
wheeled cart to
fill
their
ground
floors o
protect
their omesfrom
looding.
esidents lso said
that,
since the
1980s,
construction aste has
commonly
been used for andfill.
oday,
he ocal
clay
s more
commonly
used for other
purposes,
uch as to
temporarilyepairpaths
thathave been
submerged
and
damaged uring eavy
ains
see
photo
n
Fig.
6).
Discussion
Spatiotemporal
elationships
etween andform
and and use
In
the
study
area,
land-use
patterns
have been
transformed
ver ime
y
a
change
rom n
approach
that
adapted
to the natural andforms o one that
modified hose
andforms,
hich
orresponds
o the
Oya
(1993)
model of land-use
change
in Asian
insular oothill-rimmedowland reas.
Although
he
upland
rea had
begun
o
develop
a
strong ousing
base in
large-scale
ubdivisions n 1966
(mostly
interpreted
rom 966 aerial
photographs)
nd there
were also some businessareas being developed,
forest till overed bout31% of the surface.
n
the
low-lying
reas
at
this
ime,
esidential
and use was
largely
confined o the natural evees
and
was,
therefore,
elatively
afefrom he ffects f
flooding.
A
photograph
aken
n
1960
in a
low-lying
rea
(Fig.
8a)
shows
n
original
waterscape
hat s
typical
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GeoJournal
2008)
71:127-141
137
Fig.
8
(a)
Traditional
illage andscape long
stream nd
naturalevee andformround ite16
of
Fig.
5
in
1960
with
kind
ermission
o use
by
Nocheseda,
.I.)- fl>)
An
abandoned
wooden oat bserved
t site
of
Fig.
5
on
November
001
ofthat ime. raditionalaised-floorettlementsere
located n thebanks
fthe
tream,
nd
villagers
sed
wooden
boats s theirmain
form f
transport.
ome
of
these
lements an still e found
n
thefield
oday.
For
xample,
he
photograph
n the eft ide
of
Fig.
6
shows a traditional ooden raised-floor
welling
where he
original
pen-air
round
loorhas been
enclosed
by
a concrete lock wall.
During
ur field
survey,
e
also observed everal
bandonedwooden
boats
Fig.
8b)
in settlements
long
theroads that
have
historically
followed the natural levee
landforms.
As the regional populationhas continued o
become concentrated
n Metro
Manila,
urban and
use,
and residentialand use
in
particular,
as been
expanding
nto vulnerable reas
(Villanueva
et al.
2000)
such s theback marshes nd acustrine
lains
between henaturalevees
Midorikawa
nd Bautista
2002).
Because these andformsre
vulnerable o
flooding
JICA
2000),
the
xtensive se of andfills
essentialfor
development
f the
land
(Hara
et al.
2002).
Between
1986
and
2004,
residential reas
expanded nto the areas well beyondthe natural
levees
Figs.
2
and
4).
These residential
reas were
generally
mixture f slum
housing
and
large
subdivision
evelopments
n
fill
Woodward-Clyde
Inc.
2000;
Murakami t al.
2003).
During
his ame
period,
usiness ffices nd
large shopping
enters
were
developed
n vacant andon
the
upland
Serote
1991).
Thus,
by
2004
in
the
study
rea,
urban and
use
had
overcome he
restrictions
mposedby
the
naturalandforms.
Quantitative
nd
qualitative
haracteristics
of andfill
The use of landfill
s
by
far the most common
landform
ransformation
ractice
for
residential
development
n
low-lying
andforms
n
the
study
area
(Figs.
3 and
4).
We calculated he cumulative
volume f fill
pplied
between 966 and 2004 to be
1.95
x
105 m3
km~2,
which
represents pproxi-
mately
5.0
x
103 m3
km~2year~1
and is com-
parable
to the
rate of
fill
on the urban
fringe
f
Bangkok
(5.7
x
103m3
km 2year-1;
Hara et al.
2008).
The
material
mainly
sed for andfill
or
develop-
ment f
ow-lying
and s construction
aste,
roken
concretenparticularTable 2, Figs.5 and6). How-
ever,
according
ur field
observations
Fig.
6)
and
interviews ith ocal
inhabitants,
andfill
ractices
seem to have been variable nd to have
adapted
o
make use of themost
readily
vailable fillmaterial.
Initially,
ocal
clay
fillwas
used
to
raisethe evel of
the
ground
loors f
houses.
The
common eedto cut
off he ottom
fdoors
n
these reas
photo,
ig.
6)
is
evidence f the
gradual
nd
regular
ddition f fill.
More
recently,
andowners ave
used construction
waste
forfill
when
hey eplaced
raditional
ouses
with etached
ouses.
n
new
arge-scale
ubdivision
developments
n
low
lying
reas,
onstructionaste
used for andfill as raised he and urface o a level
higher
han the
average
and elevationof
nearby
detached ouses
Murakami
t al.
2003).
These landfill
ractices
re
presumably
or
pro-
tection
gainst looding.
ara
et al.
(2002)
reported
that
ocal residentssed whatever illwas available o
protect
heir omes
gainst looding,
nd n
doing
o,
4JÜ
pringer
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138
GeoJournal
2008)
71:127-141
they
created and-locked
lots
as
poorly
drained
swampy
and. For the maintenance
f
public
roads,
intermittent
ill renovations ave
been carried ut
without onsiderationf appropriateuilding tan-
dards,
s verified
y
staff f the
ngineering
ivision
of thePateros
municipal
ffices
n 25
August,
005.
This is
inviting
dditionalfill
practices
n
the
neighboring
ouses.
Thus in this
area,
landfill as
been
regular ractice
or
many ears,
nitially sing
local
clay
nd,
more
ecently,sing
he
arge
olumes
of broken oncrete
hathave resulted
rom
uilding
renovations.s a
result,
hebaseline f
fill
eight
as
been
gradually
aised. or
nstance,
ccording
o the
records f
road renovationn the Pateros
municipal
office,
M. Almeda
Street,
heoldest oad of
Pateros,
had been filled
with50 cm of
fill hree imes
until
1980.We calculated hetotalvolume ffillused n
the
study
rea
from
986
to
2004
(Fig.
4)
by using
the
average
fill
height
n
1986
(calculated
by
comparison
f the 1966
and
1986
topographic
aps)
as
a
baseline.
However,
on the
premise
hat the
baseline
f fill
height
as
been
gradually
aised,
he
cumulative olume
f andfill ver
the entire
eriod
from 1966
to
2004
might
be
greater
han we
calculated.
Individual
greements
asis of
fillmaterial
low
between
uppliers
nd
developers
Constructionaste,which s themostwidely sedfill
material
n the
ow-lying
reas,
ends o
flow one-to-
one
from he ource o the ite
where
t
s
used,
hat
is,
directly
rom
upplier
o end user.Wreckers
ant
to
dump
heir aste
conomically,
nd andowners
n
low-lying
reas
wantto
acquire
andfill o
develop
theirand s
cheaply
s
possible.
herefore,
one-to-
one flow
ccurs
n
the form
f a trade-off
elation-
ship.
This
relationship
evelops
on
a
case-by-case
basis,
sometimes
hroughcquaintances.
or exam-
ple,
some landowners
pen
theirvacant
lots for
dumping,
nd wreckers
an
dump
wastes
for ree r
for a small fee
(Fig.
5).
For
large-scalebuilding
renovation rojects,however,demolitionworkers
may
look for
nearbydumping
ites
by talking
o
neighbors
r relatives.
The recent
rend f urban
renewal
n the
uplands ppears
o
have resulted
n
a
considerable
ne-to-one
lowof construction
aste
and
dobe nto
ow-lying evelopmentlots.
Material
flow
f his
ype
was
not
bserved
n the
development
¥j
Springer
of
suburban
angkok
Hara
et al.
2008),
probably
because of the
greater
istances
more
han 00
km)
between he ource
nd
the
nd user.
Theflows f rushedockexcludingdobe) nd anar
intoMetroManila re
argely
ne-to-one,
ven
hough
the source
reas,
eingdependent
n
geologic
ondi-
tions,
re distant rom
development
ites. Lanar is
excavated t
Pampanga,
t the foot f Mt. Pinatubo.
Estimatedahar
roduction
romhis rea
uring
he
eak
period,
hortly
fterhe 991
ruption
ftheMt. inatubo
volcano,
was around 6.6
x
106
m3
year 1.
This
figure
s
comparable
o
the
peak
of
sand
production
for
Bangkok,
whichwas 5.5
x
107
m3
year 1
Hara
et al.
2008),
and for
okyo,
whichwas 3.0
x
107
m3
year 1
(Asahi
et al.
1993).
There is
convenient
highway
ccess to the
Pampanga egion,
romwhere
the ahar strucked,pproximately0 km othe ow-
lying evelopment
ites
n the
tudy
rea; hence,
t
s
transported
irectly
rom ource oenduse.
Although
there
re
some
ntermediateontractorsn both he
source nd end use
areas,
he
general
low s one-to-
one. This s differentrom he ituationn
Bangkok,
where ource reasfor
ill
remore han 00
km
rom
development
ites,
nd
ransport
s
via a
node-linkage
structure ith
apillary
low
owardts nduse
n
the
urban
ringe evelopment
ites.
The
structure
f the
laharflow nMetroManila s
adapted
o themacro-
scale
géomorphologieetting
f an
insular,
eolog-
ically
controlledowlandrimmed
y
volcanoes
nd
mountainousreas.This s in contrasto the ase of
Bangkok
wherematerial lowhas
adapted
o a
huge
andflat ontinentalelta
etting.
Crushed
ock s
producedmainly
rom
ayTay,
which
s
thenearest
illy
nd mountainousrea ess
than10km fromhe eastrim fMetroManila. t is
trucked
irectly
o
ow-lyingevelopmentlots
r to
local
contractors.aterite nd
clay
for andfill ave
also
been ruckedrom hese reas
directly
o the ow-
lying evelopment
reas,
lthough
he
olume
ppears
to
have
decreased
s lateritend
lay
hasbeen
eplaced
by
construction aste.These flows
f
crushed
ock,
laterite,
nd
lay
re lso
governed y
hemacro-scale
géomorphologieettingsiscussed bove.
Taking
andfill
ractice
nto onsideration
in land-use
lanning
This
study
has shown that
adaptive, unplanned
landfill
ractice
s
employed
n
ow-lying
reas.
JICA
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GeoJournal
2008)
71:127-141
139
(2000)
reported
hat hese
ractices
ause
changes
n
the
distribution
f
flood-prone
reas and
long-stand-
ing swampy lots
nd can lead to
unsanitaryiving
environments.ara et al. (2002) pointedout that
controlling
ill
height,aking
nto ccount henatural
landform
atterns,
s an effective
ay
to avoid
these
situations.
herefore,
oning
based on natural
and-
forms,
o that andfill
ractices
re
not n conflict ith
the
natural
nvironment,
s
important. ccording
o
the currentand-use
planning
ystem
n this area
(Pateros
Urban
Planning
Office
000;
Taguig City
Development Planning
Office
2003),
zoning
is
determined
y
and
essentially
parallel
with the
constructionf main roads (Fig.9), without ny
consideration
f fill
volumes hat
may
be
required.
During
ur nterviewsn
August
005,
staff t both
the ivil
engineering
nd urban
lanning
ivisions f
the
Pateros
nd
Taguigmunicipal
fficesnsisted hat
there re
effectively
o
rules
governing
he
use
of
landfill. r.
Mor P. Cabilino f the ivil
engineering
Fig.
9 The currentand-
use
plan
for
Taguig City
showing xisting
oad
network asis
zoning
Ö
Springer
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140
GeoJournal
2008)
7
1 127-141
division
f the Pateros
municipal
ffice tated
hat
landowners
eterminehe
fill
height
or heir
lots,
and
generally
match t to the
levation f
the
ccess
roadtotheir lot.The Departmentf PublicWorks
and
Highways
DPWH)
provides
national
uilding
code
DPWH 2005),
which
equires
oring
o test he
geology
nd soundness
f foundationsor
buildings
of more than
three
tories.
The Mines and Geo-
sciences
Bureau
(MGB)
of the
Department
f
Environmentnd Natural
Resources
DENR)
also
promotes
eological
and environmentalssessment
for ewurbanand
development
ith he ssuance f
DENR AdministrativerderNo. 2000-28.
Accord-
ing
to Dr. Edwin G.
Domingo,
ssistant irector t
MGB,
individual
ill
practices
evertheless
re cur-
rently
ncontrolled;
n
particular,uality
ontrol or
fillmaterialssnotfunctional.here s an mmediate
need to
develop
and
implement
zoning
scheme
based on natural
andforms,
ncorporating
oth
quantity
nd
quality
onstraints
n landfill
ractices.
Our
tudy
as revealed
hat he low f
fill
material
from ffsite ource
reas to onsite
andfill
evelop-
ment reas is
predominantly
n a one-to-one asis
using
trade-off
elationships.urrently,
hese flows
take
place independently
ithout
egulation
r
any
form
f
managementystem.
his situation
might
promote
ncontrolled rban
prawl
nd
unsanitary
urban
iving
nvironments.
evelopment
f a
system
for n effectivend
regulated
low f
fillmaterialn
Metro Manila is a task of immediatemportance.
Mapping
and
information
ystems
based on GIS
technology
hat s
being
ested
n
Japan
MLIT
2003)
and other
egions
Li
et al.
2005)
may provide
n
effectiveolution
o this
problem.
Acknowledgements
his esearch as
supportedy
Grants-
in-Aid or cientificesearch
18780017
nd
03J11839)
rom
the
Japanese inistry
f
Education, ulture,
ports,
cience
and
Technology.
e
express
ur
deep appreciation
or
help
with
ur
field
urvey
rom
Ms. Maria Florencia
.
Navera,
research
ssociate,
niversity
fthe
Philippines
os
Baños.
We
especially
ppreciate
he kind
help
of
Dr. Edwin G.
Domingo,
ssistant irector t the Mines
and Geosciences
Bureau in the
Department
f
Environmentnd Natural
Resources,and staff of Metro Manila Development
Authority,
nd he
Taguig
ndPateros
Municipal
ffices.We
also hank r.
Ryuichiro
eki
nd ther
xperts
rom
he
Japan
International
ooperation
gency
or
helping
s withour
survey.
e
especially
hank r.Elmer . Nocheseda
nd
other
local
residents,andowners,
ocal
contractors,
evelopers,
wreckers,
nd
managers
nd workers
n
sand
nd
gravel
its
for heir ind
ooperation
uring
urfield
urvey.
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This content downloaded from 121.54.54.134 on Mon, 22 Dec 2014 00:20:39 AMAll use subject to JSTOR Terms and Conditions
8/10/2019 Hara, Takeuchi, Palijon & Murakami 2008 Landfill Development in the Urban Fringe of NCR
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