muturajawela wetland (sri lanka)

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Muturajawela Wetland Kamal Prasad De Zoysa Siriwardena

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Muturajawela  Wetland  

 

 

 

Kamal  Prasad  De  Zoysa  Siriwardena  

   

  1  

 

 

Index  

1   Introduction  ..................................................................................................................  2  

2   Study  method  ...............................................................................................................  3  

3   Investigations  ...............................................................................................................  3  

3.1.   Overview  of  the  Muthurajawela  ...........................................................................  3  

3.2.   Social  and  cultural  values  .....................................................................................  4  

3.3.   Direct  economic  uses  of  wetland  resources  .........................................................  5  

3.4.   Indirect  economic  benefits  of  wetland  ecosystem  services  .................................  6  

3.5.   Flora  &  Fauna  of  Muturajawela  ............................................................................  7  

3.6.   Conservation  measures  ........................................................................................  9  

4   Finding  ..........................................................................................................................  9  

5   Recommendations  ......................................................................................................  11  

6   References  ..................................................................................................................  14  

 

 

 

 

 

 

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1 Introduction  

In  the  past,  wetlands  were  considered  as  wastelands  that  could  be  reclaimed  or  changed  for  

use   by   mankind.   Development   initiatives   have   regarded   these   areas   suited   only   for   such  

purposes,  and  as  a  consequence,  many  wetlands  have  been  drained  or  used  as  dump  sites  for  

refuse  and  urban  waste.  With  increasing  knowledge  however,  we  have  come  to  understand  that  

wetlands   are   amongst   the   world’s   most   valuable   and   vulnerable   environments   on   which   a  

variety  of  plants,  animals  and  human  communities  depend  (IUCN  Sri  Lanka,  CEA,  2006).  

Sri   Lanka   has   a   wide   array   of   inland   and   coastal   wetland   ecosystems   that   harbor   a   rich  

biological  diversity.  One  such  urban  wetland   in  Sri   Lanka   is  Muthurajawela,   the   largest  coastal  

peat  bog  of  the  island  located  on  the  West  coast.  Muthurajawela  Marsh  covers  an  area  of  3,068  

ha.   It   is   located   between   10-­‐30   km   north   of   Colombo,   in   Gampaha   District.   Together   with  

Negombo  Lagoon  (3,164  ha),  Muthurajawela  forms  an  integrated  coastal  wetland  system  of  high  

biodiversity  and  ecological  significance.  Due  to  its   importance  certain  parts  of  this  wetland  has  

been  declared  as  wildlife  sanctuary  during  1992.    

However,   despite   its   protected   status,   Muthurajawela   is   subject   to   intense   and   growing  

pressures.   Areas  within   and   surrounding   the  wetland   have   since   1991   been   zoned   for   urban,  

residential,  recreational  and  industrial  development.  Wetland  species  are  harvested  at  high  and  

often   unsustainable   levels,   land   is   being   rapidly   reclaimed   and   modified   for   agricultural,  

commercial   and   residential   purposes,   and   heavy   loads   of   industrial   and   domestic   wastes   are  

discharged  untreated  into  the  marsh.  The  wetland  area  has  been  seriously  degraded  over  time,  

and  these  threats  continue  to  intensify  (Lucy,  Kekulandala,  2003).  

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2 Study  method    

To  conduct  this  study  about  Muturajawela  I  have  visited  this  site  and  data  and  information’s  

were   collected   through   direct   observations,   face-­‐to-­‐face   interviews   and   literatures   such   as  

research  papers  etc.  

 

3 Investigations  

3.1 Overview  of  the  Muthurajawela  

Muthurajawela  is  the  largest  saline  coastal  peat  bog  in  Sri  Lanka,  located  on  the  west  coast  

(7003’N,79055’E)   between   the   Negombo   lagoon   and   Kelani   river   and   spreading   inland   upto  

Ragama   and   Peliyagoda   in   the   Gampaha   District   (Figure   1).   The   marsh,   together   with   the  

Negombo  lagoon  forms  an  integrated  coastal  wetland  ecosystem  (6,232  ha  in  total  extent).  The  

marsh-­‐lagoon  complex  is  estimated  to  have  originated  about  5000  years  BC  (CEA/  Euroconsult,  

1994).  The  main  water  source  to  the  marsh  is  Dandugan  Oya  which  drains  a  catchment  of  727  

km2  and  discharges  at  the  interface  of  the  lagoon  and  the  marsh,  while  the  marsh  is  traversed  by  

a  navigational  canal  constructed  during  the  Dutch  colonial  period.  The  area  receives  an  annual  

average  rainfall  of  2000-­‐2500mm,  while  the  average  annual  temperature  is  27oC    (Samarakoon  

and  Renken,  1999).  According  to  historical  evidence,  Muthurajawela  was  subjected  to  extensive  

cultivation  of  paddy,  more  than  500  years  ago  (GCEC/Euroconsult,  1991).  

The  Muturajawela  marsh  is  located  within  the  low  country  wet  zone  and  is  influenced  by  the  

southwest  monsoon.  The  highest  rainfall   is   received  during  the   inter-­‐monsoon  periods   in  April  

and  May,  and  in  October  and  November,  with  an  annual  rainfall  between  2,000  –  2,500  mm.  The  

soil   is   a   uniform,   potentially   acidic   sulphate,   and   the   land   is   poorly   drained   with   a   peaty  

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substrate  which  is  saturated  for  almost  the  whole  year  (IUCN,2006).      

 

3.2 Social  and  cultural  values  Around   5,000   people   live   in   or   directly   adjacent   to   Muthurajawela   marsh,   although   the  

majority   engaged   in   low-­‐paying  manual   labour   activities.  A   few   traditional   fishing   families   are  

3

Figure 1.Location of Muthurajawela wetland sanctuary

SRI LANKA

MUTHURAJAWELACOLOMBO

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involved   in   small-­‐scale  commercial  and  subsistence   fisheries   in   the  canals,   the  Dandugam  Oya  

and  marsh  lagoon  transition  zone.    The  canals  running  through  the  wetland  were  developed  and  

used  for  transportation  of  goods  during  the  Dutch  period  (Lucy,  Kekulandala,  2003).    

 

3.3 Direct  economic  uses  of  wetland  resources    

Fishing:   Between   13%   (Mahanama,   1998)   and   14%   (GCEC,   1991)   of   local   households   are  

involved  in  fishing  activities  in  the  marsh  area,  including  both  fresh  and  brackish  water  parts.  

Use   of  wetland   plants   and   trees:  Most  of   timber   species  once   found   in   the  marsh  area  have  

now  been  exploited,   and  only   small   bushy  plants   are   left   (Wijeyarate,   2000),   these  plants   are  

harvested  for  a  variety  of  purposes.  About  60%  of  houses  are  constructed  of  timber  plank  walls,  

cadjan  roof  and  cement  floor  (Mahanama,  1998),  and  make  some  use  of  wetland  species.  The  

vast  majority  of  households  an  estimated  94%  utilize  wood  fuel   for  cooking,  and  60%  of  these  

obtain  firewood  from  the  marsh  area  (Mahanama,  1998).  Reeds  and  sedges  obtained  from  the  

marsh  are  also  used  for  the  construction  of  fish  traps,  mats  and  handicrafts  (Wijeyaratne,  2000).  

Agriculture:  Due  to  the  salinity,  acidity  and  low  natural  fertility  of  its  predominantly  peat  soils,  

the  marsh  area  is  unsuitable  for  cultivating  all  but  a  very  few  crops  (GCEC,  1991).    

Recreation  and  tourism:  The  marsh  area  is  popular  recreational  destination,  primarily  attracting  

educational   or   school   trips   and   day   visitors   from  nearby   Colombo.   The  Muthurajawela   visitor  

centre  attracted  nearly  15,000  visitors  in  2000,  three  quarters  of  whom  also  took  a  boat  trip  into  

the  marsh   area.   It   is   also   estimated   that   up   to   1,500   people   are   employed   in   the   hotel   and  

restaurant  sector  in  the  area  (CEA,  1994).    

 

 

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3.4 Indirect  economic  benefits  of  wetland  ecosystem  services    

Up  to  75,000  households  or  300,000  people  live  in  the  Muthurajawela-­‐  Negombo  area,  of  which  

an  estimated  3,000  families  depend  on  fishing   in  the  Negombo  Lagoon  and  a   large  proportion  

are  employed   in   local   industries  and  businesses  or  work   in  Colombo.  Many   industries  are  also  

located  around,  and  upstream  of  Muthurajawela,  including  more  than  100  industrial  units  in  the  

area  directly  adjacent  to  the  Marsh  (GCEC,  1991).    

The  Muthurajawela   wetland   system   generates   important   indirect   functions   that   support   and  

underpin  industrial  production  and  urban  settlement  in  the  area,  including:    

Flood  attenuation:  Muthurajawela  receives  water  from  rainfall,  runoff  from  surrounding  higher  

grounds,  and  absorbs  flows  from  the  Dandugam  Oya,  Kalu  Oya  and  Kelani  Oya.  During  the  rainy  

season,   large   volumes   of   water   enter   the   wetland   system.   The   marsh   plays   an   important  

floodwater   retention   and   buffering   function   by   receiving   and   discharging   these  waters   to   the  

Negombo  Lagoon  and  the  sea  by  way  of  the  Hamilton  Canal  (CEA,  1994).      

Freshwater  recharge  and  supplies:  Water  is  supplied  to  the  wetland  system  through  the  Kelani  

Ganga   to   the   south   of   the   marsh   and   the   Dandugam   Oya   and   Ja-­‐Ela   flowing   through   the  

northern  part  of   the  marsh   to   into   the   lagoon.  Muthurajawela  acts  as  an   important   source  of  

freshwater  storage  (Mahanama,  2000).        

Sediment  and  nutrient   retention  and  wastewater  purification:  The  marsh  receives  high  loads  

of   domestic   refuse,   sewage   and   industrial   wastes,   and   sediment   and   silt   loads,   from   both  

surrounding   and  upstream  areas.   It   physically,   chemically   and  biologically   eliminates  pollution  

from   these   wastewaters.   While   wetland   plants   trap   sediments   and   remove   nutrients   and  

suspended   solids,   pollutants   and   pathogenic   organisms   accumulate   and   decompose   in   the  

wetland’s  bottom  sediments,  and  effluents  are  diluted.  Mangroves  at   the  northern  end  of   the  

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marsh  area  also  facilitate  sediment  deposition,  before  water  enters  Negombo  Lagoon.  They  act  

as   a   filter   for   through-­‐flowing   waters,   and   assist   in   the   removal   of   nutrients   and   toxic  

substances.   These   functions   play   an   important   role   in   assuring   local   water   quality,   and  

maintaining  the  quality  of  water  entering  the  lagoon  and  sea  (Lucy,  Kekulandala,  2003).  

Fish   breeding   and   nursery:   The  Muthurajawela   wetland   system   provides   indirect   support   to  

both  marsh  and  lagoon  fish  production.  Its  sheltered  waters,  flooded  vegetation  and  mangrove  

areas   all   constitute   important   breeding   grounds   and   nurseries   for   freshwater   and   marine  

species  of  fish  and  crustaceans  (Lucy,  Kekulandala,  2003).  

 

3.5 Flora  &  Fauna  of  Muturajawela    

Flora  of  Muthurajawela:  

The  Muthurajawela   wetland   sanctuary   consists   of   a   variety   of   seven  major   vegetation   types:  

marsh,   lentic   flora,   shrub   land,   reed   swamp,   grassland,   stream   bank   and  mangrove   forest.   A  

total  of  194  species  belonging  to  66  families  were  recorded  from  the  study  done  by  IUCN  during  

1999-­‐2000  and  these  included  one  endemic  species,  three  nationally  threatened  species  and  11  

invasive   alien   species.   Of   the   total   number   of   species   documented,   30   were   woody   plant  

species.    

Fauna  of  Muthurajawela:  

According  to  IUCN  study  (2000)  a  total  of  209  species  of  vertebrate  fauna,  belonging  to  

96  families  were  recorded  from  Muthurajawela.  Of  the  total  number  of  species  recorded,  17  (9  

%)   are   endemic,   while   26   (12   %)   are   nationally   threatened.   Among   the   endemic   vertebrate  

species  at  Muthurajawela,  60%  are  nationally  threatened.    

The   fish   consisted   of   40   species   (5   endemics)   belonging   to   23   families,   representing  

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approximately   45%   of   Sri   Lanka’s   native   inland   fishes.   Among   them,   5   species   are   nationally  

threatened,  while  4  are  exotic.    

The  amphibians  consisted  of  14  species  (4  endemics)  belonging  to  4  families,   including  

toads,   narrow-­‐mouthed   frogs,   aquatic   frogs   and   tree   frogs.   These   represented   approximately  

26%   of   the   total   amphibian   species   in   the   island.   Among   them,   5   species   are   nationally  

threatened.   The   Common   Toad   (Bufo  melanostictus)   and   the   Six-­‐toed   Green   Frog   (Euphlyctis  

hexadactyla)  are  very  common  species  of  amphibians  at  Muthurajawela.    

The  reptiles  consisted  of  31  species  (6  endemics)  belonging  to  18  families,  covering  20%  

of  the  island’s  reptilian  fauna.  These  included  15  species  of  tetrapod  reptiles  and  16  species  of  

serpents.   Among   the   total   species,   9   are   nationally   threatened.   The  Water  Monitor   (Varanus  

salvator),  Common  Garden  Lizard  (Calotes  versicolor),  and  two  species  of  geckos  (Hemidactylus  

frenatus  and  Gehyra  mutilata)  were  very  common  reptiles  at  Muthurajawela.    

Birds  appeared  to  be  the  dominant  group  of  vertebrates  at  Muthurajawela,  consisting  of  

102  species  (1  endemic)  belonging  to  42  families.  These  represented  approximately  37%  of  Sri  

Lanka’s  native  avifauna.  Among  the  total  species  were  19  winter  migrants,  while  3  species  are  

nationally   threatened.   About   half   of   the   bird   species   recorded   were   those   associated   with  

wetland   ecosystems,   such   as   herons,   egrets,   cormorants,   teals,   waders,   kingfishers   and   terns  

which  feed  on  aquatic  organisms.    

The   mammals   of   Muthurajawela   consist   of   22   species   (1   endemic)   belonging   to   14  

families,   representing   approximately   25%   of   the   island’s   mammalian   fauna.   Among   them,   4  

species   are   nationally   threatened.   The  murids   (rats   and  mice)  were   the  most   common   types.  

The   Slender   Loris   (Loris   tardigradus)   is   an   extremely   rare   primate   at  Muthurajawela,   and   it   is  

considered   globally   threatened.   The   marsh   is   also   an   important   refuge   for   the   carnivorous  

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Fishing  Cat  (Prionailurus  viverrinus).  

 

3.6 Conservation  measures    

In   1989   as   a   result   of   growing   concern   about   the   degradation   of   the   ecosystem,   the  

government   froze   all   public   and   private   sector   developments   within   the   marsh   until   the  

preparation   of   a   master   plan   for   sustainable   resource   use.   In   1991,   the   Greater   Colombo  

Economic  Commission  prepared   the  Master  Plan   for   the  Muthurajawela  marsh   and  Negombo  

Lagoon   wetland   complex,   which   included   a   land   use   strategy   based   on   the   wetland   being  

divided   into   zones   for   conservation,   industrial   development,   and   residential   development.   A  

detailed  plan  for  the  conservation  zone  was  prepared  following  approval  from  the  government  

in   1992.   In   1996,   1,284.45   ha   of   the   northern   section   of   Muthurajawela   were   declared   a  

Sanctuary  under  the  FFPO.  In  2004,  a  buffer  zone  (the  area  between  the  conservation  zone  and  

mixed  urban  zone)  of  285.4  ha  was  protected  as  an  EPA  under  the  NEA.  This  was  the  first  site  to  

be  declared  an  EPA  under  this  act  (Lucy,  Kekulandala,  2003).  

 

4 Finding  

Muturajawela  wetland  is  facing  various  threats  that  are  posed  by  harmful  human  activities  

and   continue   to   be   threatened   and   degraded.   Pressure   on   the   wetland   system   arise   almost  

entirely  from  human  economic  activities  in  the  surrounding  area,  and  includes:    

Habitat   deterioration   and   degradation   arising   from   land   reclamation,   clearance   of  

vegetation,   deliberate   fire,   dumping  of   garbage,   discharge  of   agrochemicals,   industrial  wastes  

and  organic  pollution.      

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Unsustainable   exploitation   of   wild   species,   including   tree-­‐felling   and   use   of   destructive  

fishing   techniques   or   over-­‐fishing   of   certain   species   or   in   certain   areas   such   as   to   supply   the  

ornamental  fish  industry.      

Introduction  of   alien   invasive  plant  and  animal   species,   including  exotic   fish,  molluscs  and  

common  house   rat;   unmanaged  domestic   animals   such   as   buffalo,   cats,   dogs,   pigs   and   goats;  

and  ornamental  plants  and  shrubs.      

Interference  with  wetland  hydrology  and  ecology   through   the   construction  of  engineering  

works,  water  diversion,  flood  control  measures  and  infrastructure  developments  such  as  roads  

and  housing.  

   

Figure  4.1,4.2:  Illegal  constructions  

 

Figure  4.3,  4.4:  Tree-­‐felling  for  use  of  destructive  fishing  techniques  

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Figure  4.5:  Garbage  dumping  

 

5 Recommendations  

Muturajawela   wetland   can   be   identified   as   one   of   the   most   valuable   and   vulnerable  

environment  on  which  a  variety  of  plants,  animals  and  human  communities  depend.  Despite  its  

protective   statues   Muturajawela   is   under   the   treat   and   it   is   necessary   to   take   appropriate  

actions   to   ensure   the   sustainable   utilization   of   this   wetland.   Conservation   of   Muthurajawela  

wetland  will  be  a  problem  without  public  participation  and  lack  of  awareness.    

A   biodiversity   status   profile   prepared   by   IUCN,   and   the   conservation   management   plan  

prepared   by   the   CEA   have   made   several   recommendations   for   conservation.   These   include  

upgrading  the  northern  part  of  the  Sanctuary  to  a  higher  protected  area  category,  clarification  

and   documentation   of   the   legal   status   of   land   ownership,   restoration   of   degraded   habitats,  

initiation  of  programmes   to  manage   the  spread  of   invasive  alien  species,  and   rehabilitation  of  

the  canal  network  to  ensure  adequate  water  seepage  to  keep  the  peaty  soils  moist  etc.  

Proposed  conservation  actions  of  IUCN,  2001  include  followings:  

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• According  the  Wetland  Sanctuary  status  as  a  Ramsar  site,  upgrading  the  protected  area  

status  of  the  northern  part  of  the  wetland  and  incorporating  additional  areas.      

• Documenting   the   legal   status   of   land   within   the   Wetland   Sanctuary,   and   the  

socioeconomic  status  of  communities  within  and  around  it.      

• Initiating  prompt  action  against  practices  that  degrade  the  wetland.      

• Initiating  restoration  activities  to  enhance  degraded  habitats.      

• Raising  awareness  on  the  importance  of  the  Muthurajawela  wetland.      

• Promoting  ecotourism.      

 

As   the  majority  of   threats   to  Muthurajawela  are  economic   in  origin,  economic  actions  are  

required   to  address   them.   Some  of   the  actions  proposed  by   IUCN,  2001  addressing  economic  

aspects  are  as  follows:  

• Taking  action  to  raise  awareness  on  the  economic  value  of  wetland  conservation.    

• Ensuring  that  wetland  values  are  factored  into  development  planning.  

• Ensure   that  economic  penalties  are   set   for  wetland  degrading  activities  at  a   level   that  

reflects  the  economic  costs  they  incur.    

• Ensuring   that   wetland   conservation   generates   tangible   economic   benefits   for  

surrounding,  poor  communities.    

• Making  efforts  to  capture  wetland  benefits  as  a  means  of  financing  conservation.    

 

 

  13  

6 References  

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