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Proceedings of International Conference on Climate Change, Biodiversity and Ecosystem Services for the Sustainable Development Goals : Policy and Practice 27-29 June 2016 at the Sirindhorn International Environmental Park, Cha-am, Phetchaburi, Thailand

(PCCA)  of  December  2015,  when  we  attempt  to  relate  climate  change  to mangroves  it  is  wise  to  adopt  a  “big  eye”  approach.  Such  an  approach  may  help  us  to  both  identify  keystone  mangrove  species  and  gaps  in  our  existing  knowledge.  Even  in  the  absence  of  global  warming  and  sea  level  rise,  global  mangrove  resources  continue  to  face  destruction  and  degradation  (Macintosh  et.  al.,  2013). With  this  threat  comes  the  pragmatic  need  for  mangrove  eco-repair,  eco-restoration  and  afforestation.  It  is  against  this  important  backdrop  that  my  paper  is  structured. II.  OVERT  AND  COVERT MANGROVE  BIODIVERSITY Some  84  trees,  shrubs  and  ferns  have  been  recognized  as  mangroves  (Saenger,  2002;  Maxwell,  2015):  an  impressive  lineup  at  the  overt  taxonomic  level.  But  how  much  of  this  biodiversity  is  necessary  to  sustain  full  ecosystem  functionality  (Maxwell,  2015)?  Indeed,  low  biodiversity  mangrove  stands,  where  one  or  a  handful  of  species  dominate  and  characterize  the  forest,  are  the  norm  globally.  This  situation  is  most  strongly  illustrated  at  the  present  biogeographic  limits  of  mangrove,  in  Japan  to  the  north  (where  Kandelia  candel  survives)  and  New  Zealand  to  the  south  (where  Avicennia  marina  survives  Maxwell,  2002).  Even  in  the  optimal  mangrove environment–in  tropical  Thailand  and  Indonesia –two  Rhizophora  species  (R.  mucronata  and  R.  apiculata)  rule  the  ecosystem.  In  both  cases, tropical  and  temperate,  good,  productive  fisheries  are  positively  associated  with  these  species-poor  yet.  ecologically  diverse  mangrove forests  (Paphavasit  et.  al.,  2009;  Maxwell,  1991).  The  direct  causal  links  may  need  more  study  as  they  are  not  always  easy  to  demonstrate  (Macintosh  et.  al.,  2013).  This  problem  is  probably  part  of  a  larger  ecological  uncertainty:  to  demonstrate  experimentally  links  between  diversity  and  ecosystem  processes  (Schulze  et.  al.,  2005;  Ives,  2007).  It  may  be  easy  (perhaps  too  easy  and  too  tempting)  to  deduce  that  because  some  mangrove  ecosystems  can  do  well  with  just  a  few  mangrove  species,  we  should  downgrade  our  worries  about  biodiversity  loss.  Such  an  “easy”  way  is  packed  with  ecological  uncertainty  and  conservation  danger.  The  danger  lies  in  the  fact  that  we  still  do  not  know  everything  we  need  to  know  about  what  species  do  in  and  for  ecosystems  and,  importantly,  how  currently  uncommon  species  fit  into  the  story.  Their  latent  eco-biological  potentials  are  unknown  in  a  world  of  climate  change. At  present,  discussion  and  documentation  in  climate  change  i s   dominated  by  the  expectation  that  global  warming  will  remain  the  trajectory  taken.  The  alternative,  global  cooling,  is  mostly  relegated  to  the  status  of  unlikely.  This  is  unwise.  A major  explosion  of  widespread  volcanism  could  easily  add  particulate  matter–volcanic  dust–to  the  Earth’s  atmosphere  resulting  in  global  cooling.  Thus,  wise  mangrove  scientists  should  also  place  cool-tolerant  mangroves  into  our  formula for  mangrove  biodiversity  awareness.  To  date,  only  two  mangrove  species  have  displayed  clear  eco-physiological  tolerance  to  ‘cold  shock’.  These  are  Avicennia  marina  and  Kandelia  candel  (Maxwell,  2002).  And  not  all  ecotypes  of  these  species  may  be  the  same  (Maxwell,  2002).  The  ecology  of  biodiversity  awaits  far  more  work.  The  discovery  of  an  unexpected  new  hybrid  mangrove  at  SIEP  by  Dr.  Sonjai  Havanond  is  another  perfectly  timed  and  welcome  reminder  for  all  in  mangrove  science  to  be  on  the  alert  for  new  genetic  diversity  and emergent  speciation.  Importantly,  the  projected  environmental  dynamics  associated  with  climate  change  may  well  contribute  to  both  extinctions  and,  in  contrast,  to  speciation  and  new  patterns  in  mangrove  forest  structure. Myers  (1988)  introduced  the  compelling  and  attractive  concept  of  biodiversity  “hotspots” into  the  literature  of  ecological  conservation  Dr.  Sonjai  Havanond’s  discovery  could  serve  to 72 Proceedings  of  the  International  Conference  on  Climate  Change,  Biodiversity  and  Ecosystem  Services  for  the Sustainable  Development  Goals  (SDGs):  Policy  and  Practice  27-29  June  2016,  Cha-am,  Phetchaburi,  Thailand


Proceedings of International Conference on Climate Change, Biodiversity and Ecosystem Services for the Sustainable Development Goals : Policy and Practice 27-29 June 2016 at the Sirindhorn International Environmental Park, Cha-am, Phetchaburi, Thailand
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