The Links between Protected Areas, Faiths, and Sacred Natural Sites
-
Upload
nigel-dudley -
Category
Documents
-
view
221 -
download
0
Transcript of The Links between Protected Areas, Faiths, and Sacred Natural Sites
![Page 1: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/1.jpg)
Essay
The Links between Protected Areas, Faiths, andSacred Natural SitesNIGEL DUDLEY,∗ LIZA HIGGINS-ZOGIB,† AND STEPHANIE MANSOURIAN‡∗Equilibrium, 47 The Quays, Cumberland Road, Bristol BS1 6UQ, United Kingdom, email [email protected]†WWF International, Avenue du Mont Blanc, CH-1196 Gland, Switzerland‡36 Mont d’Eau du Milieu, 1276 Gingins, Switzerland
Abstract: Most people follow and are influenced by some kind of spiritual faith. We examined two ways in
which religious faiths can in turn influence biodiversity conservation in protected areas. First, biodiversity
conservation is influenced through the direct and often effective protection afforded to wild species in sacred
natural sites and in seminatural habitats around religious buildings. Sacred natural sites are almost certainly
the world’s oldest form of habitat protection. Although some sacred natural sites exist inside official protected
areas, many thousands more form a largely unrecognized “shadow” conservation network in many countries
throughout the world, which can be more stringently protected than state-run reserves. Second, faiths have a
profound impact on attitudes to protection of the natural world through their philosophy, teachings, invest-
ment choices, approaches to land they control, and religious-based management systems. We considered the
interactions between faiths and protected areas with respect to all 11 mainstream faiths and to a number of
local belief systems. The close links between faiths and habitat protection offer major conservation opportuni-
ties, but also pose challenges. Bringing a sacred natural site into a national protected-area system can increase
protection for the site, but may compromise some of its spiritual values or even its conservation values. Most
protected-area managers are not trained to manage natural sites for religious purposes, but many sacred nat-
ural sites are under threat from cultural changes and habitat degradation. Decisions about whether or not to
make a sacred natural site an “official” protected area therefore need to be made on a case-by-case basis. Such
sites can play an important role in conservation inside and outside official protected areas. More information
about the conservation value of sacred lands is needed as is more informed experience in integrating these
into wider conservation strategies. In addition, many protected-area staff need training in how to manage
sensitive issues relating to faiths where important faith sites occur in protected areas.
Keywords: conservation, protected areas, religions, sacred natural sites
Enlaces entre Areas Protegidas, Creencias y Sitios Naturales Sagrados
Resumen: La mayorıa de la gente sigue y esta influıda por algun tipo de creencia espiritual. Examinamos
dos formas en que las creencias religiosas pueden influir en la conservacion de la biodiversidad en areas
protegidas. Primero, la conservacion de la biodiversidad esta influıda por la proteccion directa y a menudo
efectiva de especies silvestres en sitios naturales sagrados y en habitats seminaturales alrededor de edificios
religiosos. Los sitios naturales sagrados son la forma de proteccion de habitat mas antigua en el mundo.
Aunque algunos sitios naturales sagrados existen dentro de areas protegidas oficiales, muchos miles mas
forman una red de conservacion “sombra” no reconocida en muchos paıses, que pueden estar mas rigurosa-
mente protegidas que las areas protegidas administradas por el gobierno. Segundo, las creencias tienen un
profundo impacto sobre las actitudes de proteccion del mundo natural a traves de su filosofıa, ensenanzas,
opciones de inversion, acercamientos a la tierra que controlan y sistemas de gestion basadas en religion.
Consideramos las interacciones entre creencias y areas protegidas con respecto a las 11 creencias estableci-
das y un numero de sistemas de creencias locales. Las estrechas relaciones entre creencias y proteccion del
habitat ofrecen mayores oportunidades de conservacion, pero tambien plantean retos. La inclusion de un
Paper submitted January 16, 2007; revised manuscript accepted August 6, 2008.
568Conservation Biology, Volume 23, No. 3, 568–577C©2009 Society for Conservation BiologyDOI: 10.1111/j.1523-1739.2009.01201.x
![Page 2: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/2.jpg)
Dudley et al. 569
sitio natural sagrado en un sistema nacional de areas protegidas incrementa la proteccion para el sitio, pero
puede comprometer algunos de sus valores espirituales o sus valores de conservacion. La mayorıa de los
administradores de areas protegidas no esta entrenada para manjar sitios naturales para fines religiosos,
pero muchos sitios naturales sagrados estan amenazados por cambios culturales y degradacion del habitat.
Por lo tanto, se requiere que las decisiones sobre hacer o no que un sitio natural sagrado sea area protegida
“oficial” se tomen caso por caso. Tales sitios pueden jugar un papel importante en la conservacion dentro y
fuera de areas protegidas oficiales. Se requiere mucha informacion sobre el valor de conservacion de sitios
sagrados, ası como mas experiencia informada para integrarlos en estrategias de conservacion mas amplias.
Adicionalmente, el personal de las areas protegidas necesita capacitacion en el manejo de temas sensibles
relacionados con creencias en areas protegidas con presencia de sitios sagrados importantes.
Palabras Clave: areas protegidas, conservacion, religiones, sitios naturales sagrados
Introduction
The interplay between belief systems and nature is com-plex and deeply rooted, and provides opportunities andchallenges to biodiversity conservation. Recognition ofthe importance of conservation issues has grown enor-mously within religious communities in recent years,with statements of support coming from all 11 of theworld’s “mainstream faiths” (Palmer & Findlay 2003). Ad-ditionally, conservation institutions are recognizing therole of faiths in implementing conservation. The UN Ed-ucational, Social, and Cultural Organization (UNESCO)Man and the Biosphere Programme stresses this link (e.g.,Lee & Schaaf 2003); the UN Environment Programmecarried out a survey of sacred values in nature (Posey2002); and the Convention on Biological Diversity (Akwe2004) and The World Bank (Whitten & Morgan 2006) ad-dress faith issues. The International Union for Conserva-tion of Nature (IUCN) World Commission on ProtectedAreas has a task force on cultural and spiritual values;WWF has launched a series of “Sacred Gifts for a LivingPlanet” with faith groups to link sacred sites with con-servation; Conservation International, Flora and FaunaInternational, and The Nature Conservancy all have ini-tiatives linking conservation with religions; and the Al-liance of Religions and Conservation runs projects withfaith groups throughout the world.
Given that little over 10% of the world’s populationclaims to be nonreligious (Encyclopedia Brittanica 2005),most environmental damage is caused by faith members,and one should not exaggerate the benefits of religiousleaders espousing green issues. But this does not meanfaiths are without influence in shaping attitudes to the en-vironment. For all their appearance of constancy, mostfaiths respond to the secular world and alter aspects oftheir teachings in line with changing attitudes. One of thefastest-changing concepts within many faiths is about hu-mankind’s relationship with and responsibilities towardthe natural world (Orr 2003).
We looked at one specific but important aspect of thisrelationship: the connections between faiths and pro-
tected areas. These come in two main forms. First, thereis a tradition in many faiths of protecting sacred species,sacred natural sites, or natural landscapes around reli-gious buildings. Sacred natural sites are probably the old-est method of habitat protection, forming a large andmainly unrecognized network of sanctuaries. There hasbeen no overall survey of the world’s sacred natural sites,but regional surveys (e.g., Chatterjee et al. 2004 for In-dia) suggest that in some countries sacred natural sitesoutnumber officially protected areas, although most aremuch smaller. Participants at a UNESCO workshop inChina (UNESCO 2003) concluded that such sites oftenhave high conservation values and better protection thanlegally protected areas. Second, faiths relate to protectedareas through the more general influence they have onthe way their followers view the natural world. Faithsmay teach or require specific forms of conservation andmany manage large land areas themselves. We proposeways in which faith and conservation groups could worktogether to protect biologically important areas.
Relationship between Faiths and the Natural World
Although there are innumerable faiths and belief systems,most people subscribe to one of the 11 “mainstreamfaiths”: in alphabetical order these are Bahai, Buddhism,Christianity, Daoism, Hinduism, Islam, Jainism, Judaism,Shinto, Sikhism, and Zoroastrianism. Currently, aroundhalf the world’s population is Christian or Muslim, al-though there are many different traditions within both.
At the risk of simplification, the mainstream faiths di-vide into two broad philosophical streams with respectto nature. Faiths originating in Central and South Asia,China, and Japan (Buddhism, Daoism, Hinduism, Jain-ism, Shinto, Sikhism, and Zoroastrianism) regard natureas a critical aspect of the divinity that should be treatedwith reverence (Nasr 1996). In contrast, the three mainmonotheistic faiths that originated in the Middle East andestablished cultural domination over the Western hemi-sphere (Christianity, Judaism, and Islam) all have strong
Conservation Biology
Volume 23, No. 3, 2009
![Page 3: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/3.jpg)
570 Protected Areas, Faiths, and Conservation
teaching against idolatry and reject the concept of sacredspecies or sacred sites. Sacred groves were sometimes de-stroyed by Christian missionaries (Adler 2006) because oftheir identification with idolatry, to destroy sacred com-petitors, or even as a punishment. In an article in Science
Lynn White (1967) (a Christian) argued that Christians,Jews, and Muslims have tended to abuse the environmentbecause it has been interpreted as God’s creation to serveHumankind (White 1967). This created a strong reaction,particularly among Christians, who were the main tar-gets of White’s critique, which led among other things tostrong statements of support for the environment fromreligious leaders (e.g., Pope John Paul II [1990] and PopeBenedict XVI [2008]).
The differences between the two faith groups are sig-nificant but should not be exaggerated; there has beenmuch environmental damage in countries where faithsrevere nature as an aspect of the sacred. Conversely,monotheistic faiths have sometimes advocated forms ofland management similar to those promoted by conserva-tionists, as in the hima system, a land protection systemoriginating in the Arabian Peninsula some 1400 years agoand adopted by many Islamic societies (Kilani et al. 2007).
In recent years a large body of knowledge has built upabout links between faiths and the environment (Tucker& Grimm 1994; Tucker & Berling 2003), and studies of in-dividual faiths have been conducted (Bahai, Landau 2002;Buddhism, Tucker & Williams 1998; Christianity, North-cott 1996; Daoism, Girardot et al. 2001; Snyder 2006;Hinduism, Narayanan 2001; Islam, Bagader et al. 1994;Folz et al. 2003; Jainism, Singhvi 1990; Judaism, Vogel1999).
Sacred Nature and Biodiversity Conservation
The full meaning of sacred has challenged thinkers formillennia. Fortunately, we do not have to understand theconcept in its entirety to recognize its conservation signif-icance. But it is important to agree what might constitutesacredness in this context. For the purposes of consider-ing aspects of the natural world worthy of protection bytacit covenant within faith-based doctrine, we proposethree dimensions: sacred nature, sacred species, and sa-cred natural sites.
Sacred Nature
The most direct link between faiths and nature is thatmany faiths regard nature as imbued with sacred value.For thousands of years, humans venerated the cyclesof nature manifested in a number of ways, including aMother goddess. This tradition persists, for instance inHinduism, and the emphasis on the Virgin Mary in the or-thodox and catholic Christian faiths has also been linkedto the Mother Goddess (Warner 1976). Faiths emanat-
ing from Asia regard all nature as sacred (Gadgil & Ra-machandra 1993). Similar human-nature links have longbeen recognized in the Pacific and today are being usedto understand the environmental history of the region(Nunn 2001). The sacred aspect of nature plays an impor-tant role in Australian aboriginal worldviews and some oftheir views are crossing into the mainstream environmen-tal movement (Mulligan 2001). In the Americas the sepa-ration between humans and the rest of nature was largelyabsent in faith systems. The complex sacrificial rituals ofthe Aztecs were aimed partly at maintaining the eternalrebirth of nature (Soustelle 1961). Many North AmericanFirst Nation groups have strong regard for the naturalworld through their faiths and revere species such as thebear (Kellert et al. 1996). Recognition of sacred natureexists throughout Africa and the western Indian Oceanand is increasingly being used in conservation efforts, forexample through encouragement of taboos (e.g., Lingardet al. 2003).
Sacred Species and Individuals
Many faiths also attach importance to individual species,which are regarded as sacred or particularly sacred. Manysacred species have practical value: game animals are of-ten sacred, as are valuable plants, such as the olive (Rosen-blum 1996). Species become sacred because they arelarge or unusual, such as the baobab trees in Africa andMadagascar (Pakenham 2004) and the leopard in WestAfrica (Olupona 1993). Sacredness can be attached toa particularly old or large individual (Anderson 1969;Chandrakanth & Romm 1991). “Inspirational” speciesare sometimes regarded as sacred. For Hindus the cowdemonstrates valued attributes, such as patience, ma-ternal instincts, and gentleness. Sacredness can also besymbolic. The ancient Egyptians adopted the scarab bee-tle (Scarabaeus) as the emblem of creation because therolling dung ball that it pushed across the sand was sym-bolic of the sun’s passage in the sky (Frankfort et al.1946).
That a plant or animal is sacred does not necessarilymean humans leave it alone, but it does imply somehuman responsibility toward the species. Sacrednesscan lead directly to protection, such as that given tocrocodiles in sacred pools in Mali (Borrini-Feyerabendet al. 2004). Other sacred species are used, and manyhunting societies still believe the animals they kill are sa-cred (Lewis-Williams & Biesele 1978). For 20,000 yearsthe hunt was depicted in cave paintings that scholarslink with sacred rituals because after agriculture reducedthe necessity of the hunt painting on cave walls ceased(Mithen 2003). The hunting of the bowhead whale (Bal-
aena mysticetus) by the Inuit people of Alaska is sur-rounded by complex beliefs (Lantis 1938). The Mayorof the North Slope Borough summed these beliefs up:“The taking and sharing of the whale is our Eucharist and
Conservation Biology
Volume 23, No. 3, 2009
![Page 4: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/4.jpg)
Dudley et al. 571
Passover . . .” (Hopson 1978). Links between hunting andsacred values are not confined to indigenous peoples orpoor, rural societies. Some of the rituals associated withfox hunting in the United Kingdom stretch back to pre-Christian traditions (Howe 1981). As traditional beliefsystems break down, however, the responsibilities asso-ciated with the sacred hunt also weaken and many sacredhunt animals have suffered severe population declines.An analysis of 70 existing species-specific taboos foundthat around half apply to reptile and mammal speciesidentified as threatened in the IUCN Red List (Colding &Folke 1997). Revitalizing traditional protection strategiescan be an important conservation strategy and, for exam-ple, has recently been revived in Madagascar (Jones et al.2008).
The role of sacred trees, such as the banyan (Ficus
benghalensis) throughout southern Asia (Ingles 1995)and the kauri (Agathis australis) in New Zealand (Lew-ington & Parker 1999), has particular significance for con-servation because sacred species or individuals are oftenprotected for hundreds or even thousands of years inplaces where old-growth forests have otherwise disap-peared. Sacredness conserves both the trees themselvesand associated populations of symbiotic and parasiticspecies.
Sacred Natural Sites
The third way in which faiths contribute to conservationis through protection of “sacred natural sites.” Becausesuch sites are often maintained free from all human in-terference, their ecology can closely resemble that foundin strictly protected areas. Sacred natural sites are of-ten small, although large sacred landscapes exist (Wild& McLeod 2008). Access can be totally forbidden butis more commonly restricted, for example, to religiousleaders, although sometimes access is open to anyonewho shows respect (Wild & McLeod 2008). Not all sitesare wholly natural. The tembawang gardens of Kaliman-tan, Indonesia, are planted fruit gardens with up to 400species and also function as burial sites. In the region’sheavily modified landscapes they are the main reposi-tory of wild biodiversity and have practically the samerange and mixture of species as mature natural forests(Marjokorpi & Ruokolainen 2003). Some sacred naturalsites are important to several faiths: for example the PeakWilderness Park in Sri Lanka has significance to Muslims,Christians, Buddhists, and Hindus (Lee & Schaaf 2003).
A Survey of Sacred Natural Sites in Protected Areas
We identified sacred natural sites in over 100 countriesand focused on those in protected areas (Dudley et al.2006, see Table 1 for a subset). Sacred natural sites oc-cur in protected areas throughout the world and are not
confined to one faith, culture, or level of economic devel-opment: we found examples from Bon, Buddhist, Daoist,Christian, Hindu, Islamic, Jewish, and Shinto faiths as wellas many from traditional faiths. Although our survey wasillustrative, it is clear that traditional faiths have the mostnumerous links with protected areas. We found manyplaces of global significance to biodiversity conservation.We also found that many traditional sacred natural siteshave survived in places where most of the population hasconverted to other faiths, suggesting that the traditionalspiritual values are often retained even when people arenominally members of a mainstream faith group.
Artificial sacred sites, such as temples or shrines, cansupport important biodiversity if the surrounding area isprotected. Examples include the Angkor temple complexin Cambodia, containing the last mature forest in the re-gion, and Christian churches in Ethiopia surrounded byold trees. Sometimes, faiths recognize the conservationvalues of these areas. In Egypt the area around St. Cather-ine’s monastery, a World Heritage site, has been managedas a nature reserve since 1977, protecting several speciesendemic to the Sinai (Kamil 2002).
Importance of Sacred Natural Sites to Conservation
Over the past few years, the assumption that sacred natu-ral sites were good for biodiversity has been backed by agrowing body of evidence (Dudley et al. 2006), althoughmost research currently focuses on sacred groves.
For example, sacred groves have been assessedthroughout India. In the Jaintia Hills a sacred grove con-tains 82 tree species in 0.5 ha (Upadhaya et al. 2003)and higher than average levels of vascular plant diver-sity in three sacred groves, including 54 endemic speciesand 31 rare species (Jamir & Pandey 2003). Similarly,in the Manipur valley, there are 166 sacred groves withhigh diversity and several species confined to the groves(Devi Khumbongmayum et al. 2005). Comparable diver-sity and endemism occurs in sacred groves in south India(Ramanujam & Kadamban 2001; Ramanujam et al. 2003).Density of medicinal plants in the Western Ghats is ap-proximately twice as high in sacred groves as in govern-ment forest reserves (Boraiah et al. 2003). Sacred groveshave the highest sporocarp fungi abundance of all foresttypes (Brown et al. 2006).
Many sacred groves survive in Ghana (Chouin 2002).They are of conservation importance, but they are gen-erally less diverse than larger protected forests. Compar-ison of four sacred groves and eight unprotected treestands showed far less deforestation in the former (O’NealCampbell 2004) and higher plant diversity and fewer in-vasive species (O’Neal Campbell 2005). Although sacredgroves in Ghana have higher mammal densities than for-est reserves, they hold fewer species (Decher & Bahian
Conservation Biology
Volume 23, No. 3, 2009
![Page 5: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/5.jpg)
572 Protected Areas, Faiths, and Conservation
Tabl
e1.
Sele
cted
prot
ecte
dar
eas
that
are
also
sacr
edna
tura
lsite
s.a
Cou
ntr
yN
am
eIU
CN
cate
gory
bSiz
e(h
a)
Lin
ks
tofa
ith
s
Arg
enti
na
Lan
inN
atio
nal
Par
kII
&IV
379,
000
trad
itio
nal
;lan
do
fth
eM
apu
che
Ind
ian
so
rth
e“E
arth
peo
ple
”A
ust
ralia
Kat
aT
juta
Nat
ion
alP
ark,
(wit
hA
yers
’Ro
cko
rU
luru
)
IIan
dW
orl
dH
erit
age
Site
132,
566
trad
itio
nal
;Ulu
r um
on
olit
his
of
relig
iou
ssi
gnif
ican
ceto
Ab
ori
gin
es;s
ymb
oliz
esfe
rtili
tyan
dco
nsi
der
edth
efa
ther
and
mo
ther
of
allf
orm
so
flif
e;A
nan
gub
elie
veth
ear
eaar
ou
nd
Aye
rsR
ock
isin
hab
ited
by
do
zen
so
fan
cest
ralb
ein
gsw
ho
seac
tivi
ties
are
reco
rded
atm
any
sep
arat
esi
tes
Bh
uta
nJi
gme
Do
rjiW
ildlif
eSa
nct
uar
yIV
790,
495
Bo
nan
dB
ud
dh
ist;
Mas
ang
Kh
ang
on
eo
fm
any
ho
lym
ou
nta
ins
inB
hu
tan
,sac
red
toth
eM
asan
g,w
ho
may
hav
eo
rigi
nat
edfr
om
sou
ther
nT
ibet
Ch
ina
Xis
hu
angb
ann
aN
atio
nal
Par
kV
and
UN
ESC
OM
AB
247,
439
Bu
dd
his
t;re
serv
eis
ho
me
toa
nu
mb
ero
fm
ino
rity
gro
up
s,in
clu
din
gH
anan
dD
ai;
ever
yD
aivi
llage
con
tain
sit
so
wn
sacr
edgr
ove
;sac
red
gro
ves
pro
tect
up
to10
0,00
0h
a;X
ish
uan
gban
na
com
pri
ses
the
larg
est
and
mo
stco
mp
reh
ensi
vetr
op
ical
fore
stin
Ch
ina
Co
lom
bia
Lagu
na
de
laC
och
aR
amsa
rsi
te39
,000
trad
itio
nal
;sit
eh
asim
po
rtan
tcu
ltu
ralv
alu
efo
rth
ein
dig
eno
us
gro
up
s,w
ho
con
sid
erit
sacr
edan
du
seit
for
pu
rifi
cati
on
and
fert
ility
;lar
gely
mad
eu
po
fa
volc
anic
lake
and
surr
ou
nd
ing
hig
hla
nd
An
dea
np
eat
and
fore
st;s
ite
sup
po
rts
ad
iver
sera
nge
of
asso
ciat
edfl
ora
and
fau
na
Fin
lan
dN
ort
her
nK
arel
iaU
NES
CO
MA
Ban
d4
pro
tect
edar
eas
350,
000
Ch
rist
ian
ity;
area
con
tain
sa
nu
mb
ero
fm
on
aste
ries
fro
mth
eo
rth
od
ox
Ch
rist
ian
fait
han
dis
anim
po
rtan
tlo
cati
on
for
taig
aan
db
ore
alfo
rest
hab
itat
Ind
iaP
eriy
arT
iger
Res
erve
IIan
dIV
77,7
00H
ind
u;S
abar
imal
a,o
ne
of
Hin
du
ism
’sm
ost
po
pu
lar
pilg
rim
age
site
s,is
wit
hin
the
bo
un
dar
ies
of
sou
thIn
dia
’sP
eriy
arT
iger
Res
erve
;eac
hye
arm
illio
ns
of
dev
ote
esco
me
tow
ors
hip
Lord
Aya
pp
a;si
teis
also
anim
po
rtan
tp
rote
cted
area
Isra
elM
tC
arm
elV
and
UN
ESC
OM
AB
26,6
00Ju
dai
sm;H
a’ar
bai
mG
rove
con
tain
so
ver
80ke
rmes
oak
sw
hic
har
eco
nsi
der
edh
oly
by
loca
lres
iden
tsw
ho
gran
tth
emsp
ecia
ltre
atm
ent
and
pro
tect
ion
;are
aal
sop
rote
cts
imp
ort
ant
Med
iter
ran
ean
scru
bfo
rest
Jap
anM
ou
nt
Hak
kusa
nN
atio
nal
Par
kV
and
UN
ESC
OM
AB
14,8
26Sh
into
,Bu
dd
his
m’s
ince
717
AC
E,w
hen
Bu
dd
his
tP
ries
tT
aich
ofo
un
ded
the
Mt.
Hak
usa
nre
trea
t,kn
ow
nas
are
ligio
us
mo
un
tain
wit
ha
smal
lsec
lud
edsh
rin
eo
nto
p;n
on
wo
od
lan
dst
eep
alp
ine
scre
ensl
op
esan
dsn
ow
-slip
lan
ds
are
refu
ges
for
the
un
iqu
eA
lth
erb
osa
(co
mm
un
itie
sw
ith
tall
her
bac
eou
sp
lan
ts,e
spec
ially
ind
enu
ded
fore
star
eas)
Ken
yaM
ou
nt
Ken
yaII
142,
020
trad
itio
nal
;reg
ard
edas
ah
oly
mo
un
tain
by
the
Kik
uyu
and
Mer
ulo
cal
com
mu
nit
ies;
rem
nan
tar
eao
fra
info
rest
,wit
hh
igh
wild
life
valu
e;p
rote
cts
wat
ersh
edsu
pp
lyin
gd
rin
kin
gw
ater
toN
airo
bi
Mal
awi
Nyi
kaN
atio
nal
Par
kII
3,13
4(k
m2)
trad
itio
nal
;sev
eral
sacr
edsi
tes
imp
ort
ant
for
rain
mak
ing
cere
mo
nie
s,w
hic
hst
illta
kep
lace
;on
eo
fth
ela
rges
th
igh
gras
slan
dp
late
aus
inA
fric
a;h
asa
hig
hle
velo
fen
dem
ism
con
tin
ued
Conservation Biology
Volume 23, No. 3, 2009
![Page 6: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/6.jpg)
Dudley et al. 573
Tabl
e1.
(con
tinue
d)
Cou
ntr
yN
am
eIU
CN
cate
gory
bSiz
e(h
a)
Lin
ks
tofa
ith
s
Mal
aysi
aK
inab
alu
Nat
ion
alP
ark
II75
,370
trad
itio
nal
;Kad
azan
Du
sun
peo
ple
wh
oliv
eo
nM
tK
inab
alu
bel
ieve
mo
un
tain
issa
cred
bec
ause
itis
the
rest
ing
pla
cefo
rth
eir
ance
sto
rs’s
pir
its;
par
kco
nta
ins
ah
igh
nu
mb
ero
fen
dem
icfl
ora
Nep
alSa
garm
ath
aN
atio
nal
Par
kII
and
Wo
rld
Her
itag
eSi
te11
4,80
0B
ud
dh
ism
;Sh
erp
asb
elie
vego
ats,
yaks
,an
dsh
eep
are
un
der
the
spec
ialp
rote
ctio
no
fK
hu
mb
uY
ulL
ha,
the
pro
tect
or
dei
tyo
fth
eK
hu
mb
ure
gio
n;s
ever
alm
on
aste
ries
inth
ep
ark;
area
con
tain
sim
po
rtan
tw
ildlif
esp
ecie
s,in
clu
din
g15
2sp
ecie
so
fb
ird
so
fw
hic
h36
are
bre
edin
gsp
ecie
sfo
rw
hic
hN
epal
may
ho
ldin
tern
atio
nal
lyim
po
rtan
tp
op
ula
tio
ns
New
Zea
lan
dT
on
gari
roN
atio
nal
Par
kII
and
Wo
rld
Her
itag
eSi
te76
,504
trad
itio
nal
;fir
stn
atu
rals
ite
toal
sob
ere
cogn
ized
for
its
spir
itu
alim
po
rtan
ceto
the
Mao
rip
eop
le;s
acre
dm
ou
nta
ino
fth
eN
gati
Tu
wh
aret
oa
loca
ted
inth
ep
ark
Nig
eria
Sacr
edG
rove
so
fO
sho
gbo
Wo
rld
Her
itag
esi
te55
trad
itio
nal
;5sa
cred
spac
esin
gro
ves
and
9w
ors
hip
po
ints
alo
ng
the
rive
rth
atru
ns
thro
ugh
the
site
;40
shri
nes
and
2p
alac
es;o
ne
of
the
few
rem
nan
tso
fh
igh
pri
mar
yra
info
rest
inN
iger
ia;s
up
po
rts
ad
iver
sefl
ora
and
fau
na,
incl
ud
ing
end
ange
red
wh
ite-
thro
ated
mo
nke
y(C
erc
opit
hecu
sery
thro
ga
ster)
Per
uH
isto
ric
San
ctu
ary
of
Mac
hu
Pic
chu
VI
32,5
92tr
adit
ion
al;s
pec
tacl
edb
ear
(Tre
ma
rcto
sorn
atu
s)in
Mac
hu
Pic
chu
tho
ugh
tto
serv
eas
am
esse
nge
rb
etw
een
the
spir
its
of
the
hig
hel
evat
ion
san
dth
ose
of
the
jun
gle
and
itis
ath
reat
ened
spec
ies
Ru
ssia
nFe
der
atio
nY
uga
nsk
iyK
anth
yIa
648,
700
Ch
rist
ian
ity;
pro
tect
edar
eacr
eate
dar
ou
nd
Lake
Nu
mto
—a
Kh
anty
and
Nen
ets
sacr
edp
lace
—in
Bel
oya
rsk
regi
on
SriL
anka
Pea
kW
ilder
nes
sP
ark
IV22
,380
Isla
m,B
ud
dh
ism
,Hin
du
ism
,Ch
rist
ian
ity;
mo
un
tain
bel
ieve
dto
con
tain
asa
cred
foo
tpri
nt
that
has
valu
efo
rat
leas
t4
fait
hgr
ou
ps
and
isa
maj
or
site
of
pilg
rim
age;
on
eo
fth
eri
ches
tar
eas
of
bio
div
ersi
tyo
nth
eis
lan
dSw
eden
Lap
on
ian
area
Wo
rld
Her
itag
eSi
te94
0,00
0tr
adit
ion
al;S
amip
eop
lep
erce
ive
the
wo
rld
asa
livin
g,in
terc
on
nec
ted
enti
tyin
wh
ich
hu
man
bei
ngs
are
on
ep
art
of
man
yan
dp
ract
ice
ash
aman
isti
csp
irit
ual
ity;
lan
dit
self
con
sid
ered
sacr
ed;c
on
tain
sa
hig
hly
imp
ort
ant
net
wo
rko
fb
iod
iver
sity
rese
rves
Tan
zan
iaM
isal
iIsl
and
Mar
ine
Co
nse
rvat
ion
Are
aV
I2,
158
Isla
m;M
isal
iIsl
and
con
sid
ered
of
hig
hsa
cred
valu
eb
ecau
seit
ssh
ape
po
ints
tow
ard
Mec
caan
db
ecau
seH
adh
ara,
aM
usl
imp
rop
het
,is
bel
ieve
dto
hav
ep
raye
dth
ere
usi
ng
the
gro
un
das
ap
raye
rm
at;s
ust
ain
able
use
of
fish
ing
reso
urc
esis
per
mit
ted
Un
ited
Stat
eso
fA
mer
ica
Co
con
ino
Nat
ion
alFo
rest
VI
747,
061
trad
itio
nal
;San
Fran
cisc
oP
eaks
wit
hin
the
nat
ion
alfo
rest
are
sacr
edto
13In
dia
ntr
ibes
;am
on
gth
e4
mo
stsa
cred
pla
ces
for
the
Nav
ajo
Ind
ian
s,w
ho
use
itto
colle
ctm
edic
inal
pla
nts
and
togr
eet
thei
rsp
irit
san
dfi
nd
pat
hw
ays
for
thei
rp
raye
rs
aM
ain
sou
rce:D
udle
yet
al.
(20
06
).bK
ey:IU
CN
,In
tern
ati
on
alU
nio
nfo
rC
on
serv
ati
on
of
Na
ture
;U
NE
SC
O,U
nit
ed
Na
tion
sE
du
cati
on
al,
Sci
en
tifi
ca
nd
Cu
ltu
ralO
rga
nis
ati
on
;M
AB
,U
nit
ed
Na
tion
sU
NE
SC
OM
an
an
dth
e
Bio
sph
ere
Pro
gra
m.
Conservation Biology
Volume 23, No. 3, 2009
![Page 7: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/7.jpg)
574 Protected Areas, Faiths, and Conservation
1999). Similarly, these Ghanian groves contain lower den-sities of butterflies than forest reserves, although both arericher than surrounding areas (Bossart et al. 2006).
Results of research elsewhere demonstrate the rich-ness of sacred natural sites. In Kalimantan, Indonesia,sacred sites play an important role in forest conserva-tion (Wadley & Colfer 2004), as do traditional Feng Shuiwoods in Hong Kong (Marafa 2003), sacred groves inmainland China (Anderson et al. 2005), and sacred forestsin Mozambique (Virtanen 2002).
Sacred groves can thus contain important remnant bio-diversity, which can be significant to conservation strate-gies in the absence of other habitat. Because they aregenerally small, their diversity is often less than in largerprotected areas, unless care has been taken to maintainparticular groups, such as medicinal plants, or if condi-tions support rare species. Studies similar to those citedabove are needed of other sacred sites that focus on whatwild species are or are not protected, whether the man-agement of sacred natural sites is secure, and how suchsites contribute to wider conservation strategies.
Managing for Faith and Nature
Protected-area managers and conservation planners needto address faith issues in three main areas. They need to(1) improve management for sacred values inside existingprotected areas where sacred natural or built sites alreadyexist, (2) look at options for integrating other sacred ar-eas more effectively within broadscale conservation ap-proaches, and (3) work out how faiths can contribute toefforts to develop ecologically representative protectedarea networks.
Sacred Sites Inside Protected Areas
Most protected-area managers are trained in natural re-source management and a systematic approach to sci-ence, which is not enough to manage sacred sites. Ap-proaches must be sensitive and based on qualitative un-derstanding, along with recognition and tolerance of be-liefs. The manager will often be of a different faith groupand therefore reliant on faith leaders to help determinehow a particular feature should be managed.
One implication of the existence of sacred sites in pro-tected areas is a potential need for trade-offs betweenconservation and spiritual values. Large-scale pilgrimagesthrough national parks, as in Cota de Donana NationalPark in Spain (Mallarach & Papayannis 2007), can createecological stress, and ritual hunting may be important fora faith group but a problem if the species is endangered.Zoning sacred sites is a challenge in faiths where theirlocation is secret, as for instance with the Baka peoplein the Congo Basin (Dudley et al. 2006). Visitors can in-terfere with sacred sites (Digance 2003). Management
for faith values can take a disproportionate amount oftime. In many cases staff will need training and access tospecialized guidelines (e.g., Wild & McLeod 2008) .
Sacred Sites and Broader Conservation Strategies
For sacred natural sites or biologically rich areas aroundbuilt sacred sites with a potential conservation role, sev-eral options exist. Sacred sites can be gazetted as part orall of a protected area or managed outside protected areasas buffer zones, corridors, or community conserved ar-eas. Ideally the most suitable option should be selected inthe context of wider regional conservation plans. A num-ber of governance approaches are available, with varyingamounts of control devolved to communities (Borrini-Feyerabend et al. 2004).
A key decision is whether to gazette a sacred naturalsite as a protected area or to leave it as an “unofficial”community conserved area. Governments may supportgazettement because this increases protected-area cov-erage with little effort. Conservation organizations tendto be enthusiastic because sacred natural sites often rep-resent secure protected areas. But what are the costsand benefits for the faiths? Becoming an official pro-tected area can bring supportive policy and legislation,extra resources, and increased options for ecotourism.In Xishuangbanna, China recognition of biodiversity val-ues means local communities have been able to attractresources for managing holy hills that they have pro-tected for centuries (Sochaczewski 1999). Nevertheless,protected-area status often means loss of control and at-tracts more attention to the site. Even where commu-nities retain a management role, additional stakeholderscan lead to a loss of influence. In Australia Kata TjutaNational Park contains Uluru (Ayers Rock), an importantsacred site for the Anangu people (Layton 1989), but de-spite being under the control of traditional owners it hasproved difficult to stop visitors from climbing on the rock(James 2007). The benefits of recognizing a sacred natu-ral site as a protected area depends on how managementand governance are approached; the needs and strengthsof traditional owners; the site’s biological value; whetherit fits IUCN’s definition of a protected area; its potentialrole in conservation strategies; what protected area sta-tus offers; and whether the government will recognize itin the national system.
Many faith communities, however, are recognizing thebenefits of protection status. The cultures supportingmany sacred natural sites are fragile and changing fast;ancient sites are often now under pressure or disappear-ing. For example, the number of sacred groves in theKodagu District of the Western Ghats, India, declinedby 59% last century (Chandrakanth et al. 2004). Wheremembers of a community want to maintain the integrity
Conservation Biology
Volume 23, No. 3, 2009
![Page 8: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/8.jpg)
Dudley et al. 575
and values of a site, converting it into a protected areacan often help its survival. The kaya forests of coastal EastAfrica are remnants of a rich and endangered ecosystemthat also has high spiritual value. These forests are be-ing incorporated into protected areas with the supportof local communities, who are concerned about themdisappearing (Burgess & Clarke 2000).
Broader Contribution of Faiths to Conservation
Recognition and protection of sacred natural sites is animportant conservation strategy, but it is limited to a rel-atively small area in global terms. A potentially muchlarger contribution could come from cooperation be-tween mainstream faiths and conservation organizationswith respect to the former’s investment policies, landownership, and management approaches. For example,the International Interfaith Investment Group is workingwith religious organizations from many faiths to changeinvestment policies, collectively worth US$7000 billion(International Interfaith Investment Group 2007), so thatthey will include investments that favor conservation.As owners of large areas of land, faith groups can alsoembrace more conservation-oriented approaches them-selves. A network of private protected areas, owned andmanaged by faith groups, could add substantially to globalconservation efforts and help bring conservation issuesto the fore in faith communities.
Conclusions
Many sacred natural sites can contribute to biodiversityconservation strategies. Whether this is most effectivelyachieved by incorporating them inside a protected areaor integrating them less officially as part of wider con-servation strategies needs to be determined individually.Effective decisions need to involve all relevant stakehold-ers (i.e., faith groups on the impacts to sacred values andconservationists on the site’s usefulness as a protectedarea). Protecting natural areas with sacred significancealso protects cultures and traditions that have existed forcenturies.
More generally, conservation organizations need towork much more closely with faith groups to identifyeffective ways to collaborate in terms of both land man-agement and investment decisions. Further research isrequired, particularly about the location and status ofsacred natural sites and about the quantitative data onbenefits to conservation, including effective monitoringsystems. Finally, faith groups and conservation organi-zations need to continue and increase the cooperationthat has emerged recently. Protected-area managers andconservation organizations must recognize the legitimacy
of sacred values of nature, improve training in these is-sues, and work cooperatively with faith groups to ensurethat spiritual and cultural values are effectively preservedwithin protected areas. At the same time, faith leaderscould increase their contributions to the historic aim ofcompleting an ecologically representative system of pro-tected areas by committing a proportion of the land andwater they control to this purpose.
Acknowledgments
We have benefited greatly from many people withinWWF, The World Bank, and the Alliance of Religions andConservation. Case studies for the report on which thepaper is based came from S. Chatterjee, J.M. Mallarach, M.Palmer, D. Rose, S. Stolton, I. Wisbono, and He Xiaoxin,with F. Asmar, A. Githitho, H.F.M. Khalid, J. Kreidi, P.G.Krishnan, Dr. Manoharan, A.K. Thani, S. Wells, and Dayakcommunities of Gunung Lumut, Indonesia. The followingpeople commented on the text: J. Bowling, P. Chatter-ton, N. Cox, A. Ekobo, V. Finlay, P. Gerard, S. Kalem,K. MacKinnon, L. Padfield, N. Ratsifandrihamanana, K.Rakovska, J. Smith, R. Soutter, L. Usongo, and A. Whit-ten. We are grateful to three reviewers of an earlier draftwho did much to improve its coherence. Research wassupported by WWF and the World Bank as part of the “Ar-guments for Protection” project, which aims to identifyand quantify benefits from protected areas.
Literature Cited
Adler, J. 2006. Cultivating wilderness: environmentalism and legaciesof early Christian asceticism. Comparative Studies of Society andHistory 48:4–37.
Anderson, D. M., J. Salick, R. K. Moseley, and X. K Ou. 2005. Conservingthe sacred medicine mountains: a vegetation analysis of Tibetansacred sites in northwest Yunnan. Biodiversity and Conservation14:3065–3091.
Anderson, E. N. 1969. Sacred fish. Man 4:443–449.Akwe. 2004. Akwe: Kon. Convention on Biological Diversity, Montreal.Encyclopedia Brittanica. 2005. Worldwide adherents of all religions by
six continental areas, Mid-2005. Encyclopedia Brittanica, London.International Interfaith Investment Group (IIIG). 2007. Annual Report
2006. IIIG, Amsterdam.Bagader, A. A., A. T. Al-Chirazi El-Sabbagh, M. As-Sayyid Al-Glayand, and
M. Y. Izzi-Deen Samarrai. 1994. Environmental protection in Islam.Environmental policy and law paper 20. R International Union forConservation of Nature, Gland, Switzerland, and Cambridge, UnitedKingdom.
Boraiah, K. T., R. Vasudeva, S. A. Bhagwat, and C. G. Kushalappa.2003. Do informally managed sacred groves have higher richnessand regeneration of medicinal plants than state-managed reserveforests? Current Science 84:804–808.
Borrini-Feyerabend, G., A. Kothari, and G. Oviedo. 2004. Indigenous andlocal communities and protected areas. Cardiff University, Cardiff,and IUCN, Gland, Switzerland, and Cambridge, United Kingdom.
Bossart, J., E. Opuni-Frimpong, S. Kuudaar, and E. Nkrumah. 2006.Complementarity of fruit-feeding butterfly species in relict sacredforests and forest reserves of Ghana. Biodiversity and Conservation15:333–359.
Conservation Biology
Volume 23, No. 3, 2009
![Page 9: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/9.jpg)
576 Protected Areas, Faiths, and Conservation
Brown, N., S. Bhagwat, and S. Wilkinson. 2006. Macrofungal diversityin fragmented and disturbed forests of the Western Ghats of India.Journal of Applied Ecology 43:11–17.
Burgess, N. D., and G. P. Clarke, editors. 2000. Coastal Forests of EasternAfrica. IUCN, Gland, Switzerland, and Cambridge, United Kingdom.
Chandrakanth, M. G., M. G. Bhat, and M. S. Accavva. 2004. Socio-economic changes and sacred groves in South India: protectinga community-based resource management institution. Natural Re-sources Forum 28:102–111.
Chandrakanth, M. G., and J. Romm. 1991. Sacred forests, secular forestsand people’s actions. Journal of Natural Resources 31:741–756.
Chatterjee, S., Y. Gokhale, K. C. Malhotra, and S. Srivastava. 2004. Sa-cred groves in India: an overview. Indira Gandhi Rashtriya ManavSangrahalaya, Bhopal.
Chouin, G. 2002. Sacred groves in history: pathways to the social shap-ing of forest landscapes in coastal Ghana. IDS Bulletin 33:39–46.
Colding, J., and C. Folke. 1997. The relations among threatened species,their protection, and taboos. Ecology and Society 1:http://www.consecol.org/vol1/iss1/art6/ (accessed February 2009).
Decher, J., and L. K. Bahian. 1999. Diversity and structure of terrestrialsmall mammal communities in different vegetation types on theAccra Plains of Ghana. Journal of Zoology 247:395.
Devi Khumbongmayum, A., K. M. L. Ashalata, and R. Tripathi. 2005.Sacred groves of Manipur, northeast India: biodiversity value, statusand strategies for their conservation. Biodiversity and Conservation14:1541–1582.
Digance, J. 2003. Pilgrimage at contested sites. Annals of Tourism Re-search 30:143–159.
Dudley, N., L. Higgins-Zogib, and S. Mansourian. 2006. Beyond be-lief: linking faiths and protected areas for biodiversity conservation.WWF and Alliance of Religions and Conservation, Gland, Switzer-land.
Foltz, R., F. M. Denny, and A. Baharuddin. 2003. Islam and ecology: a be-stowed trust. Harvard University Press, Cambridge, Massachusetts.
Frankfort, H., H. A. Frankfort, J. A. Wilson, and T. Jacobsen. 1946. Theintellectual adventure of ancient man. University of Chicago Press,Chicago, Illinois.
Gadgil, M., and G. Ramachandra. 1993. This fissured land: an ecologicalhistory of India. Oxford University Press, Delhi.
Girardot, N., J. Miller, and L. Xiaogan, editors. 2001. Daoism and ecol-ogy: ways within a cosmic landscape. Harvard University Press,Cambridge, Massachusetts.
Hopson, E. 1978. The people of the whales: a fight for survival. IndianAffairs 98:7–8.
Howe, J. 1981. Fox hunting as ritual. American Ethnologist 8:278–300.Ingles, A. 1995. Religious beliefs and rituals in Nepal. Page 210 in P.
Halladay and D. A. Gilmour, editors. Conserving biodiversity outsideprotected areas: the role of traditional agro-ecosystems. IUCN, For-est Conservation Programme, Gland, Switzerland, and Cambridge,United Kingdom.
James, S. 2007. Constructing the climb: visitor decision-making at Uluru.Geographical Research 45:398–407.
Jamir, S. A., and H. N. Pandey. 2003. Vascular plant diversity in thesacred groves of Jaintia Hills in northeast India. Biodiversity andConservation 12:1497–1512.
Jones, J., M. M. Andriamarovololona, and N. Hockley. 2008. The im-portance of taboos and social norms to conservation in Madagascar.Conservation Biology 22:976–986
Kamil, J. 2002. Al-Ahram Weekly July. 25–31.Kellert, S. R., M. Black, C. R. Rush, and A. J. Bath. 1996. Human culture
and large carnivore conservation in North America. ConservationBiology 10:977–990.
Kilani, H., A. Serhal, and O. Llewellyn. 2007. Al-Hima: a way of life.International Union for Conservation of Nature West Asia RegionalOffice, Amman, Jordan, and the Society for the Protection of Naturein Lebanon, Beirut, Lebanon.
Landau, R. 2002. The Baha’i faith and the environment. In P. Tim-
merman, editor. Encyclopedia of global environmental change. Vol-ume 5, social and economic dimensions of global environmentalchange. John Wiley and Sons, London. Available from http://bahai-library.com/articles/landau.environment.html (accessed February2009).
Lantis, M. 1938. The Alaskan whale hunt and its affinities. AmericanAnthropologist 40:438–464.
Layton, R. 1989. Uluru: an Aboriginal history of Ayers Rock. Reprintededition with additions. Aboriginal Studies Press, Canberra, Australia.
Lee, C., and T. Schaaf, editors. 2003. The importance of sacred natu-ral sites for biodiversity conservation. UN Educational, Social andCultural Organization, Paris.
Lewington, A., and E. Parker. 1999. Ancient trees: trees that live for athousand years. Collins and Brown, London.
Lewis-Williams, J. D., and M. Biesele. 1978. Eland hunting ritualsamong northern and southern San groups: striking similarities.Africa 48:117–134.
Lingard, L., N. Raharison, E. Rabakonandrianina, J. A. Rakotoarisoa, andT. Elmqvist. 2003. The role of local taboos in conservation and man-agement of species: the radiated tortoise in southern Madagascar.Conservation and Society 1:223–246.
Mallarach, J. M., and T. Papayannis, editors. 2007. Protected areasand spirituality: proceedings of the first workshop of the DelosInitiative—Montserrat 2006. IUCN, Gland, Switzerland.
Marafa, L. 2003. Integrating natural and cultural heritage: the advantageof feng shui landscape resources. International Journal of HeritageStudies 9:307–323.
Marjokorpi, A., and K. Ruokolainen. 2003. The role of traditional forestgardens in the conservation of tree species in West Kalimantan,Indonesia. Biodiversity and Conservation 12:799–822.
Mithen, S. 2003. After the ice: a global human history 20,000–5000 BC.Weidenfeld and Nicholson, London.
Mulligan, M. 2001. Re-enchanting conservation work: reflections on theAustralian experience. Environmental Values 10:19–33.
Narayanan, V. 2001. Water, wood, and wisdom: ecological perspectivesfrom the Hindu traditions. Daedalus, American Academy of Arts andScience, Cambridge, Massachusetts.
Nasr, S. H. 1996. Religion and the order of nature: the 1994 Cadburylectures at the University of Birmingham. Oxford University Press,Oxford, United Kingdom.
Northcott, M. S. 1996. The environment and Christian ethics. Cam-bridge University Press, Cambridge, United Kingdom.
Nunn, P. D. 2001. On the convergence of myth and reality: exam-ples from the Pacific islands. The Geographical Journal 167:125–138.
Olupona, J. K. 1993. Some notes on animal symbolism in African religionand culture. Anthropology and Humanism 18:3–12.
O’Neal Campbell, M. 2004. Traditional forest protection and wood-lots in the coastal savannah of Ghana. Environmental Conservation31:225–232.
O’Neal Campbell, M. 2005. Sacred groves for forest conservation inGhana’s coastal savannas: assessing ecological and social dimen-sions. Singapore Journal of Tropical Geography 26:151.
Orr, M. 2003. Environmental decline and the rise of religion. Zygon38:895–910.
Pakenham, T. 2004. The remarkable baobab. Weidenfeld and Nichol-son, London.
Palmer, M., and V. Finlay. 2003. Faith in conservation. The World Bank,Washington, D.C.
Pope Benedict XVI. 2008. Address by his Holiness Benedict XVI. Banga-roo, Sydney, Australia. 17 July. Holy See, Vatican City. Available fromhttp://www.vatican.va/holy_father/benedict_xvi/speeches/2008/july/documents/hf_ben-xvi_spe_20080717_barangaroo_en.html(accessed August 2008).
Pope John Paul II. 1990. The ecological crisis: a common responsibil-ity. Peace with God The Creator, peace with all of creation. Mes-sage of His Holiness for the celebration of the World Day of Peace.
Conservation Biology
Volume 23, No. 3, 2009
![Page 10: The Links between Protected Areas, Faiths, and Sacred Natural Sites](https://reader036.fdocuments.in/reader036/viewer/2022081806/575066311a28ab0f07a5c1d8/html5/thumbnails/10.jpg)
Dudley et al. 577
Catholic Conservation Center, Wading Bridge, New York. Avail-able from http://conservation.catholic.org/ecologicalcrisis.htm (ac-cessed May 2008).
Posey, D. A., editor. 2002. Cultural and spiritual values of biodiversity.UN Environment Programme and Intermediate Technology Publica-tions, Reading, United Kingdom.
Ramanujam, M. P., and D. Kadamban. 2001. Plant biodiversity of twotropical dry evergreen forests in the Pondicherry region of SouthIndia and the role of belief systems in their conservation. Biodiversityand Conservation 10:1203–1217.
Ramanujam, M. P., K. Praveen, and K. Cyril. 2003. Woody species di-versity of 4 sacred groves in the Pondicherry region of South India.Biodiversity and Conservation 12:289–299.
Rosenblum, M. 1996. Olives: the life and lore of a noble fruit. AbsolutePress, London.
Singhvi, L. M. 1990. The jain declaration on nature. Jainism GlobalResource Center, Alpharetta, Georgia. Available from http://www.jainworld.com/jainbooks/Books/Jaindecl.htm (accessed May 2008).
Snyder, S. 2006. Chinese traditions and ecology: survey article. World-views, Environment, Culture and Religion 10:100–134.
Sochaczewski, P. 1999. Life reserves, opportunities to use spiritual val-ues and partnerships in forest conservation. Pages 137–143 in S.Stolton and N. Dudley, editors. Partnerships for protection. Earth-scan, London.
Soustelle, J. 1961. The daily life of the Aztecs. George Weidenfeld andNicolson, London
Tucker, M. E., and J. Berling. 2003. Worldly wonder: religions entertheir ecological phase. Open Court Publishing, Chicago, Illinois.
Tucker, M. E., and J. Grimm. 1994. Worldviews and ecology: religion,philosophy and the environment. Orbis Books, Maryknoll, NewYork.
Tucker, M. E., and D. R. Williams, editors. 1998. Buddhism and ecology:the interconnection of Dharma and Deeds. Harvard University Press,Cambridge, Massachusetts.
UNESCO (UN Educational, Social and Cultural Organization). 2003.Linking universal and local values: managing a sustainable futurefor World Heritage. World Heritage papers 13. UNESCO, Paris.
Upadhaya, K., H. N. Pandey, P. S. Law, and R. S. Tripathi. 2003. Treediversity in sacred groves of the Jaintia hills in Meghalaya, northeastIndia. Biodiversity and Conservation 12:583–597.
Virtanen, P. 2002. The role of customary institutions in the conservationof biodiversity: sacred forests in Mozambique. Environmental Values11:227–241.
Vogel, D. 1999. How green is Judaism? University of California,Berkeley.
Wadley, R. L., and C. J. P. Colfer. 2004. Sacred forest, hunting, and con-servation in West Kalimantan, Indonesia. Human Ecology 32:313–338.
Warner, M. 1976. Alone of all her sex: the myth and the cult of theVirgin Mary. Vintage, London.
White, L. 1967. Historical roots of our ecologic crisis. Science155:1203–1207.
Whitten, T., and B. Morgan, editors. 2006. Faiths and the environment:World Bank support 2000–2005. The World Bank, Washington, D.C.
Wild, R., and C. McLeod, editors. 2008. Sacred natural sites: guidelinesfor protected area managers. IUCN, Gland, Switzerland.
Conservation Biology
Volume 23, No. 3, 2009