Republic of the Philippines Republic Act 7611 PALAWAN COUNCIL FOR SUSTAINABLE DEVELOPMENT Puerto Princesa City Environmental Profile, Palawan, 2014 1 Palawan Environmental Profile, 2014 Table of Contents 1.0 BIOPHYSICAL ENVIRONMENT .............................................................................. 4 1.1 Physical Ecosystem ....................................................................................................... 4 1.11 Land Area............................................................................................................ 4 1.12 Topography ......................................................................................................... 4 1.13 Land Classification ............................................................................................. 4 Environmentally Critical Areas Network ....................................................................... 7 ECAN Zones: Terrestrial Component, as of 2007 ...................................................... 7 Updated ECAN Zones: Coastal Marine Zone, as of 2007 .......................................... 8 1.2 Terrestrial Ecosystem.................................................................................................... 9 Land Cover...................................................................................................................... 9 Watersheds/Catchment ................................................................................................. 11 Communal Forest .......................................................................................................... 13 Caves ............................................................................................................................. 13 Community-based forest management ......................................................................... 18 Other Tenured areas ...................................................................................................... 18 Solid Waste ................................................................................................................... 18 1.3Coastal-Marine Ecosystem .......................................................................................... 18 Coral Reefs.................................................................................................................... 18 Mangrove Resources ..................................................................................................... 26 Seagrass/seaweeds .................................................................................................... 34 Live Reef Fish ........................................................................................................... 34 Marine Protected Areas (tina) ....................................................................................... 37 Pearl Farms ............................................................................................................... 48 1.5 Protected Areas ........................................................................................................... 49 Puerto Princesa Subterranean River National Park .................................................. 50 Tubbataha Reef National Marine Park ..................................................................... 51 Calauit Game Preserve and Wildlife Sanctuary........................................................ 52 Ursula Island Game Refuge and Bird Sanctuary ...................................................... 53 El Nido-Taytay Managed Resource Protected Area ................................................. 54 The Malampaya Sound Protected Landscape and Seascape.................................... 55 The Coron Island Protected Area .............................................................................. 56 Tabon Caves Complex .............................................................................................. 58 Mt. Mantalingahan Protected Landscape .................................................................. 58 Palawan Flora, Fauna and Watershed Reserve ......................................................... 58 Wildlife ......................................................................................................................... 58 Flora: Palawan List of Threatened Species ............................................................... 58 Fauna: Palawan List of Threatened Species ............................................................. 59 Invasive Alien Species .............................................................................................. 64 II SOCIO-CULTURAL & POLITICAL ENVIRONMENT ............................................ 64 Indigenous Peoples ........................................................Error! Bookmark not defined. 2 List of Palawan Indigenous Communities & Estimated Population .................. Error! Bookmark not defined. Tribal Ancestal Zones / Ancestral Domain Claims ...Error! Bookmark not defined. III. ECONOMIC ENVIRONMENT ..................................Error! Bookmark not defined. Mining and Mineral Development .....................................Error! Bookmark not defined. Gravel and Sand Quarry.............................................Error! Bookmark not defined. PCSD Approved Projects for the year 2010-2013 .....Error! Bookmark not defined. Agriculture .....................................................................Error! Bookmark not defined. Petroleum/Hydrocarbon (Oil & Gas) Development ......Error! Bookmark not defined. Oil and Gas ...............................................................Error! Bookmark not defined. Energy and Power ......................................................Error! Bookmark not defined. Water ..........................................................................Error! Bookmark not defined. Agriculture .................................................................Error! Bookmark not defined. Tourism ......................................................................Error! Bookmark not defined. INFRASTRUCTURE ....................................................Error! Bookmark not defined. Communication ..........................................................Error! Bookmark not defined. Transport ....................................................................Error! Bookmark not defined. Education ...................................................................Error! Bookmark not defined. ELECTRICITY and Power ........................................Error! Bookmark not defined. Water ..........................................................................Error! Bookmark not defined. Challenges, Research Gaps ............................................Error! Bookmark not defined. 3 1.0 BIOPHYSICAL ENVIRONMENT 1.1 Physical Ecosystem 1.11 Land Area 1,489,626 hectares1 1,456,743 hectares2 1.12 Topography Slope: Flatlands (0-8%) - ___ hectares or __% Rolling (8-18%) - ____ 1.13 Land Classification Status of Land Classification: 2012 (in hectares)3 Total Area Certified A&D PALAWAN 1,489,626 453,700 Forest Land Classification ReservTn Timberland National Civil Parks Resrvn 1,035,926 71,394 171,832 767,320 25,380 Total Total Area Puerto Princesa City 2,381.02 sq. km 238,020 hectares Certified A&D 15 % Unclassified Public Forest Timberland 74% 11% Note: Based on the data of National Mapping and Resource Information Authority (NAMRIA) cite reference here 1 Philippine Forestry Statistics, Bureau of Forestry Development Land area generated/computed made by PCSDS-GIS upon generation of the ECAN zones map 3 Philippine Forestry Statistics, Bureau of Forestry Development 2 4 Municipality Aborlan Agutaya Araceli Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Cuyo Culion Dumaran El Nido Kalayaan Is. Linapacan Magsaysay Narra Quezon Rizal Roxas San Vicente Taytay Sofronio Española Puerto Princesa City TOTAL Land Area Hectares Sq. Km. 807.33 37.31 204.30 581.60 726.20 1,303.40 392.90 26.39 689.10 84.95 499.59 435.00 923.26 290.00 195.44 49.48 831.73 943.19 1,256.47 1,177.56 1,462.94 1,257.68 473.91 2,381.02 17,030.8 Classification Number of Barangays4 2nd 5th 19 10 13 20 2nd 1st 22 18 14 12 23 17 14 16 18 1 10 11 23 5th 1st 4th 1st 5th 5th 1st 1st 14 11 31 10 31 9 66 Sources: National Statistics Office, National Statistical Coordination Board, Department of Finance and Land Management Bureau, Department of Environment and Natural Resources. Notes: 1. Land area based on the 2007 Revised Masterlist certified by the Land Management Bureau (LMB). 2. Classification and number of barangays based on NSCB Philippine Geographic Classification (PSGC) as provided by the Bureau of Local Government Finance (BLGF). Provincial Profile –Palawan. Retrieved May 13,2014, from http://nsor4b.webs.com/provincial%20profile/Palawan/Palawan_c1.html 4 5 Name Rearrange this table Code Income Class City Class Population Land (as of May Area 2010) “ Land Registered Population Area District (as of Voters 1 (as of May (2013) (2010) 1, 2010) 2007, in hectares) “ “ Income Class (delete the Code) ABORLAN AGUTAYA ARACELI BALABAC BATARAZA BROOKE’S POINT 1. ABORLAN 175301000 1st 3rd 17,995 32,209 80,733 2. AGUTAYA 175302000 5th 1st 5,711 11,906 3,731 3. ARACELI 175303000 4th 1st 7,525 14,113 20,430 4. BALABAC 175304000 2nd 2nd 18,114 35,758 58,160 5. BATARAZA 175305000 1st 2nd 30,361 63,644 72,620 6. BROOKE'S POINT 175306000 1st 2nd 32,109 61,301 130,340 7. BUSUANGA 175307000 3rd 1st 11,144 21,358 39,290 5,055 7,116 2,639 8. CAGAYANCILLO 175308000 6th 1st 9. CORON 175309000 1st 1st 21,811 42,941 68,910 10. CUYO 175310000 4th 1st 11,350 21,847 8,495 11. DUMARAN 175311000 3rd 1st 11,855 21,397 43,500 12. EL NIDO (BACUIT) 175312000 1st 1st 17,910 36,191 92,326 13. 175313000 5th 1st 8,275 14,180 19,544 6 LINAPACAN 14. MAGSAYSAY 175314000 5th 1st 6,527 11,965 4,948 15. NARRA 175315000 1st 2nd 32,455 65,264 83,173 135,417 222,673 238,102 16. PUERTO PRINCESA 175316000 CITY (Capital) Highly Urbanized 1st 3rd 17. QUEZON 175317000 1st 2nd 25,947 55,142 94,319 18. ROXAS 175318000 1st 1st 36,636 61,058 117,756 19. SAN VICENTE 175319000 1st 1st 18,123 30,919 146,294 20. TAYTAY 175320000 1st 1st 34,030 70,837 125,768 21. KALAYAAN 175321000 5th 1st 299 222 29,000 22. CULION 175322000 3rd 1st 10,233 19,543 49,959 23. RIZAL 175323000 1st 2nd 18,948 42,759 125,647 24. SOFRONIO ESPAÑOLA 175324000 2nd 2nd 17,449 29,997 47,391 National Statistical Coordination Board – Active Stats Palawan. Retrieved May 13,2014, from http://www.nscb.gov.ph/activestats/psgc/province.asp?provcode=175300000 Environmentally Critical Areas Network ECAN Zones: Terrestrial Component, as of 2007 CITY / MUNICIPALITY CORE ZONE Hectares ABORLAN AGUTAYA ARACELI BALABAC BATARAZA BUSUANGA BROOKE'S POINT CAGAYANCILLO CORON* CULION CUYO DUMARAN EL NIDO ESPAÑOLA 25,157 13 2,995 11,762 16,553 7,423 25,975 30 15,071 13,498 10 15,879 16,893 9,289 % 34 0 17 21 21 19 38 2 20 35 0 30 37 18 RESTRICTED CONTROLLED TRADITIONAL Hectares Hectares Hectares 1,617 2 0 557 2,761 3,098 565 0 343 350 272 0 8,395 1,021 % 2 0 0 1 4 8 1 0 0 1 4 0 19 2 19,695 108 2,714 6,965 13,154 5,932 6,108 55 14,152 103 3 16,093 969 5,207 % 26 1 15 12 17 15 9 4 19 0 0 30 2 10 2,661 1,180 11,871 7,022 3,396 3,767 7,612 940 24,131 8,759 794 9,029 16,905 9,632 MULTIPLE % Hectares 4 14 68 13 4 9 11 76 32 23 12 17 37 19 25,211 1,841 0 29,556 34,437 19,544 27,932 204 11,499 16,198 3,248 12,496 1,925 25,273 7 % 34 22 0 53 45 49 41 17 15 42 48 23 4 50 JOSE RIZAL KALAYAAN LINAPACAN MAGSAYSAY NARRA PUERTO PRINCESA CITY QUEZON ROXAS SAN VICENTE TAYTAY TOTAL PER ZONE 64,177 0 810 111 20,741 102,666 28,571 36,166 7,849 27,303 448,941 970 5 1,361 18 4,332 50 0 5 2 23 46 30 37 11 20 53,569 3,022 4,130 12,553 23,647 122,589 30.3 1 12 9 0 5 24 3 4 17 17 17,708 1 4,360 3 19,214 14,683 14,940 18,952 29,643 29,625 240,387 8.3 14 3 28 0 21 7 16 19 40 21 9,847 1 5,885 1,432 8,635 3,412 8,635 115 3,759 27,768 177,188 16.2 8 3 38 26 9 2 9 0 5 20 34,856 25 3,182 3,093 38,497 50,176 38,500 38,346 20,202 31,397 467,638 11.9 COASTAL ZONES (Has) Core ABORLAN AGUTAYA ARACELI BALABAC BATARAZA BUSUANGA BROOKE'S POINT CAGAYANCILLO CORON* CULION CUYO DUMARAN EL NIDO ESPAÑOLA JOSE RIZAL KALAYAAN LINAPACAN MAGSAYSAY NARRA PUERTO PRINCESA CITY QUEZON ROXAS SAN VICENTE TAYTAY TOTAL PER ZONE Transition 55 5,240 6,978 34 314 SPECIAL ZONE (Has) Sustainable 170 938 1,424 653 Protected Area 3,667 7 243 TOTAL Tribal/Ancestr. 5,732 685 748 7,590 8,301 1,598 3,667 5,732 0.5 0.6 0.1 0.2 0.4 64 20 55 42 22 41 39 27 22 31.5 Updated ECAN Zones: Coastal Marine Zone, as of 2007 CITY / MUNICIPALITY 27 74,341 8,439 17,580 55,862 77,313 39,764 68,192 1,229 75,702 38,908 6,718 53,497 45,087 50,422 127,558 39 15,598 5,585 91,419 224,506 94,416 97,709 74,006 139,740 1,483,632 8 1.2 Terrestrial Ecosystem Land Cover As of 2005 of the 1,448,676 hectares total land area of the province, recent data derived from 2005 satellite images indicates that Palawan forest accounts for 666,338 hectares or about forty-six percent (46%) of the terrestrial area. 5 Forest cover is measured by accounting for the forested area relative to the total terrestrial area. Land Cover, Palawan Province, 1992 and 2005 Land Cover Category Forest Primary/Old growth forest Secondary/Residual forest Mossy forest Marginal forest Ultramatic forest Karst/limestone forest Mangrove forest Open Mangrove Brushland Grassland Agricultural areas Paddy field Coconut plantation Other plantation Cropland Orchard Kaingin/Barren Built-up areas Roads Fishpond/Saltpond Bares/Rocky area Mining area River Wetlands/Water Body/Lake Clouds/Shadow Total 5 6 1992 (JAFTA) Hectares % 2005 (PCSDS) Hectares % 738,886 333,380 335,893 40,864 27,651 0 1,098 50,602 0 245,585 252,025 91,053 42,893 26,697 7,942 13,821 0 0 1,083 0 170 9,507 1,468 0 1,179 35,138 52.1 23.5 23.7 2.9 2.0 0.1 3.5 17.2 17.7 6.4 3.0 1.0 0.6 0.9 0.1 0.0 0.7 0.1 0.1 2.5 666,338 189,772 373,278 21,601 41,935 26,993 12,759 58,400 2,807 444,123 55,727 194,066 64,003 56,031 35,917 22,459 14,164 1,644 10,080 6,166 2,279 1,045 737 4,208 1,801 - 46.0 13.1 25.8 1.5 2.9 1.9 0.9 4.0 0.2 30.7 3.9 13.4 4.4 3.9 2.3 1.6 1.0 0.1 0.7 0.4 0.2 0.1 0.1 0.3 0.1 - 1,426,796 100.0 1,448,676 100.0 Change6 % (6.1) 0.5 0.2 13.5 (13.9) 7.0 0.6 0.4 0.2 (0.6) (0.1) 0.3 0.0 (2.5) State of the Environment 2004 - 2009 State of the Environment 2004-2009 9 Land Cover7 7 State of Environment 2004-2009 10 Forest Cover, By Municipality 1992 and 20058 City/Municipality 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. 13. 14. 15. 16. 17. 18. 19. 20. 21. 22. 23. Aborlan Agutaya Araceli Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Culion Cuyo Dumaran El Nido Espanolda Linapacan Magsaysay Narra Quezon Puerto Princesa City San Vicente Rizal Roxas Taytay Total 1992 (JAFTA) Hectares % 46,395 63 0 112 1 14,742 27 22,813 34 25,940 41 21,047 49 0 26,212 40 18,333 43 0 18,281 32 23,502 39 15,198 30 4,253 37 0 46,509 56 56,992 62 155,832 73 50,058 68 91,359 72 47,402 47 53,906 44 738,886 2005 (PCSDS) Hectares 42,274 84 17,964 15,792 24,611 14,823 87 26,011 13,884 27 9,242 23,621 7,419 5,579 0.4 36,118 43,706 159,135 54,672 73,912 47,147 50,232 666,338 % 57.1 4.8 32.4 23.0 36.1 33.1 8.7 37.0 31.1 0.6 19.4 43.3 17.0 39.0 0.01 45.7 46.8 72.1 75.2 58.1 46.5 36.1 Change 1992-2005 (4,121) 84 (112) 3,222 (7,021) (1,329) (6,224) 87 (201) (4,449) 27 (9,039) 119 (7,779) 1,326 0 (10,391) (13,286) 3,303 4,614 (17,447) (255) (3,674) (72,548) As manifested in Table 1. a forest gain of 50,410 hectares was achieved from 1992 to 1998 or an equivalent rate of increase of 8,402ha/year. As indicated on Table 1, brushland increased from 17.21 to 21.03 percent of the total terrestrial area or an increase of approximately 51,668 hectares.9 Watersheds/Catchment River Systems and Surface Waters (Discuss here the river water quality monitoring, including maps.) 8 9 State of Environment State of Environment 2004-2009 11 The PCSDS conducts regular monitoring of the major river systems of Palawan as part of its activities under the Environmental Monitoring and Evaluation System. In order to determine the condition of these river systems in relation to the local communities' use for household or domestic purposes, the 26 river systems were evaluated as to their conformity or suitability to freshwater Class A or Public Water Supply Class II. In the process of evaluation, nine (9) parameters were used in determining the water quality index of the river systems: pH, dissolved oxygen, total suspended solids, total dissolved solids, oil and grease, biochemical oxygen demand, phosphates, nitrates and total coliform. The following table presents the results of analysis: Index Rating vis-à-vis Remarks** Freshwater Class A* As of 2009 As of 2013 Fair => Marginal Aborlan River 72 58 Aborlan Marginal => Marginal Iraan River 64 52 Marginal Talakaigan Dam 63 Fair => Marginal Ipilan River 68 51 Fair => Marginal Maasin River 67 53 Fair => Fair Tamlang Dam 79 73 Brooke's Point Marginal => Fair Tigaplan River 64 70 Marginal Sabsaban River 60 Marginal Tagdidili River 61 Fair Pangobilian River 70 Fair => Marginal Aramaywan River 75 59 Marginal => Marginal Balitien River 57 54 Fair => Marginal Batang-batang River 68 59 Narra Marginal => Marginal Bato-bato River 61 57 Fair => Marginal Cabuluan River 65 49 Marginal => Marginal Calategas River 59 52 Good => Marginal Calategas Dam 82 64 Fair Batang-batang Dam 72 Fair => Marginal Cabayugan River 70 57 Puerto Princesa City Fair => Marginal Bacungan River 73 50 Fair => Marginal Irawan downstream 67 62 Marginal Irawan upstream 64 Fair => Marginal Berong River 65 52 Quezon Marginal => Marginal Ibat-ong River 61 60 Fair => Marginal Panitian River 65 57 Fair => Marginal Tagbung-saing Lake 69 58 Marginal => Marginal Guineratan River 63 48 Roxas Marginal Magara upstream 59 Marginal Magara downstream 48 San Vicente Fair => Marginal Inandeng River 75 50 Marginal => Marginal Labog River 53 52 Sofronio Española Marginal => Marginal Pulot downstream 57 46 Marginal Pulot Dam 59 Marginal => Marginal Abongan River (upstream) 63 57 Taytay Marginal Ibangley River 51 Marginal Abongan River (downstream) 56 * Freshwater Class A per DENR-AO 34,s.1990, pertains to Public Water Supply Class II -for sources of water supply that require complete treatment in order to meet the National Standard for Drinking Water (NSDW). Index rating of river systems range from Poor (1-44) to Excellent (95-100). ** The applicable categories of water quality, description of ranks and associated index ranges are the following: Municipality River System Good – water quality is protected but occasionally threatened or impaired. Conditions under certain water classification rarely depart from natural or desirable quality. (Index Range: 80-94). Fair – a single water use under certain water classification may be temporarily interrupted; conditions sometimes depart from desirable quality as required under certain water classification. (Index Range: 65-79). 12 Marginal – water quality under certain water classification is frequently threatened or impaired, conditions often depart from desirable quality as required under certain water classification. (Index Range: 45-64). Communal Forest Caves Caves are integral part of our ecosystem. It has diverse value to our country even if they are rarely seen by people and even if many of them have remained undiscovered. They serve as habitat of unique, rare, endangered and even unknown plants and animals. They contain important geological formations and deposits of great beauty generally termed as speleothem and speleogen. Caves have paleontological values as they contain fossils which are the preserved remains of prehistoric plants and animals and they tell us nearly all we know about the history of life on Earth. Caves are also culturally, archaeologically, historically and spiritually significant areas. In ages, past humans made use of caves as shelter and they leave behind artifacts (e.g. tools, pottery, and coffins), ecofacts (e.g. human and animal bones) and artworks on the walls proving their existence and way of life. Caves, even now, serve as burial grounds and sites of religious practices and rituals. Caves such as Tabon Cave Complex (municipality of Quezon) and Ille Karst Tower (municipality of El Nido) are examples of such significance. Caves maybe located in public or private land and within ancestral domain/land. PCSD Administrative Order No. 03-08 and its Implementing Rules and Regulations govern the management, protection and conservation of caves in the province of Palawan. Caves and cave resources may be used for scientific, economic, ecotourism and other purposes based on the assessment and classification led by the PCSD and its staff. 13 At present, there are 64 caves (2009-2010) identified by the PCSDS in the province of Palawan. The local DENR-PAWS have also identified 26 caves (as of December 2008) since the inception of the Caves Act in 2001. These caves are distributed throughout the mainland and islands of the province. The locations of these identified caves are reflected on the PCSD “Cave Distribution Map” developed by the staff (see Distribution Map of Selected Caves). Identified caves in the municipalities of Busuanga, Taytay, El Nido, Cuyo and Cagayancillo are mainly utilized for economic purposes such as edible bird’s nests gathering/collection and ecotourism. The most popular among our caves is the Saint Paul Subterranean River National Park in Sitio Malapien, Bgy. Cabayugan, Puerto Princesa City. Another is the Tabon Cave Complex in Lipuun Point, municipality of Quezon wherein human remains (Tabon man) dating to 47,000 years ago was recovered from a cave known as Tabon. Among the 64 identified caves in the province of Palawan (2009-2010), 11 caves were assessed, mapped and recommended for classification to the PCSD by the PCSDS cave assessment team. 14 15 16 Kuyba Almonica, San Jose, Puerto Princesa City Moore’s Cave, Bgy. Panalingaan, Rizal Gangub Caves of Bgy. Sandoval, Bataraza 17 Community-based forest management Other Tenured areas Solid Waste 1.3Coastal-Marine Ecosystem Coral Reefs hard calcareous skeletons of tiny sea animals living in tropical waters, that 10often form reefs often appear rock-like, but are actually colonies of living organisms have symbiotic relationship with small photosynthetic algae (zooxanthellae) that live in the tissue of polyp o essential for coral life o sufficient light for photosynthesis is a requirement for survival of corals, algae, also absorb waste from the polyps, and via photosynthesis, incorporate the nutrients into the polyp tissues Coral reefs are built up entirely by biological activity o each coral polyp builds limestone skeleton by extracting o ca from seawater rich sources of food: animals and plants a.k.a oasis of the ocean o very high productivity and supply nutrients to the vast oceans have low nutrients and energy Ecological Importance extremely efficient in capturing nutrients and sunlight 10 PCSD Coastal Resource Monitoring (CRM) 18 a. cycled for use of many different organisms generate much of beach sand in the Philippines fringing reef offers an effective protection of the shoreline against the constant pounding of waves Most importantly a breeding ground and habitat for a wide variety of organisms including invertebrates and fish. Types of Coral Reefs 1. Barrier reefs 2. Fringing reefs 3. Atoll reefs Enemies of the Corals 1. Man use of explosive materials and bottom trawl in fishing 2. Spiny starfish or Crown-of-thorns (Acanthaster planci) destroy coral reefs by foraging on coral polyps recently observed to multiply in great numbers 3. Sedimentation a major factor in the destruction of corals in lesser amount, may interfere with the feeding processes inhibit the release of larvae interfere with photosynthesis Based on the graph above, the number of sites in poor condition has more than doubled within a decade. This can be attributed to the number of sites with excellent, good and fair condition dropping from 1.7% to 14.7% which would mean there was an increase of sites in poor condition. 19 Old Classification New Classification The pie chart above shows the old classification of coral condition against the new classification. Sites in excellent condition was the same for the two classification. Sites in good condition in the old classification also did not change in value but changed in category in the new classification into Very good condition. The most significant change with these two classification is that the sites in poor condition in the old classification reduced by more than half in the new classification. The new classification describes the condition of coral reef to be equally distributed in the chart aside from the excellent category while the old classification describes the province to have almost half of sites to be in poor condition. Live Coral Cover (LCC) Condition/Category Municipality Year # Sites Excellent Good Fair Poor 76-100% 51-75% 26-50% 0-25% 1. Aborlan 2013 19 2. Agutaya 2009 22 15.8 0 31.6 0 26.3 5 26.3 95 3. Araceli 2012 12 0 33.33 33.33 33.33 4. Balabac 2011, 2012 22 0 7.1 49.5 43.4 5. Bataraza 2012 23 0 26.1 65.2 8.7 20 6. Brooke’s Point 2008 9 0 55.6 22.2 22.2 7. Busuanga 2003, 2011 1,202 2.7 14.8 18.6 63.9 8. Cagayancillo 2007 12 0 75 16.7 8.3 1,965 0.6 1.0 19.1 79.3 3+ 4.6 17.6 39.2 38.7 9. Coron 10. Culion 2003, 2011 2004, 2011 11. Cuyo 2010 20 0 0 0 100 12. Dumaran 2010, 2011 28 7.4 32.1 39.2 21.2 13. El Nido 2004 No data 0 3 7 90 14. Linapacan 2004, 2011 40 0 2.9 51.2 45.8 15. Magsaysay 2009 18 0 0 11.1 88.9 16. Narra 2013 24 4.2 25 45.8 25 17 .Puerto Princesa City 2005 2,793 0 2.5 6 91.5 18. Quezon 2005 4 0 60.9 39.1 0 19. Rizal 2011 21 0 66 24 10 20. Roxas 2004 22 9.1 50 40.9 0 21. San Vicente 2005, 2011 1,286 0.0 3.2 4.8 92.0 22. Sofronio Española 2011 26 0 7.7 57.7 34.6 23. Taytay 2011, 2012 15 0.7 8.7 64.7 25.9 24. Tubbataha 2004 3 55.79 43.21 24.2 30.4 Overall MEAN 7,565+ 2.0 45.4 The table above shows the current condition of the sites per municipality. As for the majority of the municipalities, the graph shows the dominance of the sites in poor 21 condition (Violet bar). The municipality of Roxas, Cagayancillo and Quezon however does not share the same condition and has none of its sites in poor condition. It is worth noting that with the 3 sites in Tubbataha, the over all condition is in good condition. Live fish and coral reef fishery is not very good Only 20.3% are in good-excellent condition, with 79.8% in poor-fair condition The worst and poorest coral reefs conditions can be found in the municipalities of cuyo (100%), agutaya (95%), el nido (90%), Magsaysay (88%), quezon (75% and in the city of Puerto princesa (91.5%)11 Reef Condition by Category, Palawan 2011. Excellent 1.1% Good 19.2% Poor 45.7% Fair 34.1% 11 National and Provincial Policy, Regulation and Enforcement The Palawan Live Reef Food Fish Trade 22 A number of studies on the condition of the coral reef of Palawan have been and are being currently done throughout the Island-Province of Palawan by different organizations and institutions, both government or private. The Palawan Council for Sustainable Development Staff has done its own baseline assessment and monitoring of the province’s coral reefs since the advent of the SEP Law or Republic Act 7611 in the 1990s. Coastal resource assessments or CRA were done in almost every municipality to assess and have baseline data on the status of mangrove forests, seagrass meadows, reef fishes and the coral reefs. The PCSDS 1st CRA was done in 1997 in the Municipality of Sofronio Española, signaling the start of CRA in different municipalities. Subsequently, coastal resource monitoring (CRM) was undertaken after 4 years in the case of the Municipality of Sofronio Espanola, and 7-9 years in other municipalities depending on the means of the municipality to complement the activity. Unfortunately, CRM was not conducted in all of the municipalities where CRA was done due to operational and logistical limitations of PCSDS. A compilation of PCSDS and other related studies were shown in Table 1 describing the status and/or conditions of coral reefs throughout the province. Data gathered are assessments made by the PCSDS, the SEMP-NP ECAN Zoning Sub-component and other sources such as the WWF. The PCSDS has not yet conducted any/surveys or assessments regarding coastal resources in the Municipality of Kalayaan. The descriptive result of each survey was used to describe the general state of coral reef conditions since each survey differs in methodology, so as to be objective in the general result. POOR = 0-25% FAIR 26-50% = GOOD = 51-75% EXCELLENT = 76-100% (English et.al, 1997) 23 Table 1.Palawan Coral Reef Baseline Data Municipality Aborlan Araceli Agutaya Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Culion Cuyo Dumaran El Nido Linapacan Magsaysay Narra Quezon Rizal Roxas San Vicente S. Española Taytay No. of Survey % HC % SC Sites 1998 4 35.15 11.24 2000 11 21.83 29.83 2002 22 31.25 0.22 2006 35.8 3.9 2003 24 47.52 9.10 2001 7 19.32 30.33 1999 22 28.23 2.62 2007 12 42.53 12.24 1999 6 1999 17 30.81 2.99 2003 22 40.54 5.66 2001 28 36.42 1.22 11 2002 (eastern part 20.64 1.94 only) 2004 34 26.6 3.0 2001 18 38.66 4.03 1997 9 42.17 8.31 2005 2001 17 52.07 3.31 2003 21 47.11 2.04 2000 26 34.40 11.55 2000 22 33.27 2.95 1997 9 42.57 9.53 13 2001 48.4 2.94 ( only) Year Description/ Condition 46.39 FAIR* 51.66 GOOD* 31.46 FAIR* 39.7 FAIR***** 56.62 GOOD* 49.65 FAIR* 30.85 FAIR* 54.77 GOOD* *** 33.80 FAIR* 46.23 FAIR* 37.64 FAIR* Total 22.58 POOR* 29.6 POOR** 42.69 FAIR* 50.48 GOOD* POOR** 55.38 GOOD* 49.15 FAIR* 45.95 FAIR* 36.22 FAIR* 52.10 GOOD* 51.34 GOOD** * PCSDS Coastal Resource Assessments and Monitoring ** SEMP-NP ECAN Zoning Component Surveys *** Rapid Marine Biodiversity Assessment – CI & PCSDS **** World Wildlife Fund (WWF)-WPU ***** Sulu-Sulawesi Seascape Project 24 Table 2. Coral Reef Status, in Selected Municipalities of Palawan, through time Municipality Aborlan Araceli Agutaya Brooke’s Point Busuanga Coron Culion Cuyo Dumaran El Nido Magsaysay Narra Quezon Roxas San Vicente S. Española Taytay 1st Description/ 2nd Description/ % HC % SC Total % HC % SC Total Monitoring Condition Monitoring Condition 2003 44.39 8.35 52.74 GOOD* 2005 22.97 5.77 28.74 FAIR* 2010 18.95 9.87 28.82 FAIR**** 2009 9.90 1.35 11.16 POOR* 2008 17.93 22.66 40.59 FAIR* 2003 2003 2000 2010 2010 2004 2009 2003 2005 2004 2005 2001 2004 POOR** POOR** 41.87 FAIR***** 6.03 POOR* 39.06 FAIR POOR** 15.98 POOR* 53.20 GOOD* 51.54 GOOD* 56.17 GOOD* - POOR** 47.41 FAIR* 49.91 FAIR** 3.56 38.33 2.47 0.73 11.51 43.89 48.82 51.47 38.76 46.97 4.63 9.22 2.72 4.70 8.65 2.94 2004 POOR** 2010 20.35 0.88 21.23 POOR**** 2010 31.55 1.74 33.28 FAIR**** * PCSDS Coastal Resource Assessments and Monitoring ** SEMP-NP ECAN Zoning Component Surveys ***Rapid Marine Biodiversity Assessment – CI & PCSDS **** WWF-WPU ***** HAYUMA Foundation 25 Mangrove Resources12 Number of True Mangrove Species Found per Municipality While there were a total of 28 true mangrove species recorded in the Philippines (Field Guide to the Identification of Some Mangrove Plant Species in the Philippines-Ecosystem Research and Development Service, Region 7, Fishery Sector Program-DENR) under 19 families, monitoring and baseline assessments conducted in the mangrove forests of twenty (20) municipalities out of twenty-four (24) municipalities of the province of Palawan revealed a total of twenty-three (23) mangrove species belonging to eleven (11) families. The table below shows the number of mangrove species recorded per municipality as of 2004 during the baseline assessments and as of 2014 during the monitoring assessments. There are some municipalities which increase the number of recorded mangrove species while there are some which decrease. These changes may be attributed to species recruitment wherein propagules of certain mangrove species were transported to particular area by sea current and wave action, deposited and grow. Other factors such as geomorphological characteristics of the soil, sunlight intensity, exposure, etc. contributed much to the survival of propagules and presence of mangrove species. On the other hand, the decrease in the number of species may be due to its very limited distribution. Some of the municipalities were not yet monitored as of 2014. Municipalities Aborlan Araceli Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Culion Cuyo Dumaran El Nido Española Linapacan Magsaysay Narra Quezon Rizal Roxas San Vicente 12 Number of Species (as of 2004) 15 13 14 10 24 18 18 10 17 19 16 18 8 15 9 13 17 18 Number of Species (as of 2014) 19 12 27 17 11 21 9 17 18 11 19 16 17 18 - PCSDS Coastal Monitoring Resource (CMR) 26 Taytay AVERAGE 20 15 20 17 30 25 20 Number of Species (as of 2004) 15 Number of Species (as of 2014) 10 5 Ab or l Ar a n ac Ba eli la ba B Br oo ata c ke raz ’s a P Bu oi n Ca su t ga ang ya a nc illo Co ro Cu n lio n C Du u yo m ar El an N Es id p o Li a ño na la M pa ag ca sa n ys ay Na Q rra ue zo n Ri za Sa Ro l x n Vi as ce nt T e AV ay ER ta y AG E 0 Species Diversity Index The species diversity of mangrove forests is being measured through Shannon Weiner Biodiversity Index. As shown in table below, there is only slight difference between the mangrove species diversity index of the municipalities monitored. Using the Biodiversity Scale developed by Dr. Edwino Fernando in 1998 as indicated below: Shannon (H’) Index 3.5 and above 3.0 - 3.49 2.5 - 2.99 2.0 - 2.49 1.99 and below Very high biodiversity High Moderate Low Very low 27 All the mangrove forests of the municipalities in the province manifested very low species diversity. Municipalities Aborlan Araceli Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Culion Cuyo Dumaran El Nido Española Linapacan Magsaysay Narra Quezon Rizal Roxas San Vicente Taytay AVERAGE Shannon Weiner Index (ave. as of 2004) 1.17 0 1.15 1.16 1.50 1.37 1.00 0.99 1.04 1.01 1.27 1.02 1.12 1.21 0.72 1.14 1.00 0.94 1.01 1.10 Shannon Weiner Index (ave. as of 2014) 1.78 1.20 1.31 1.30 1.74 1.00 0.94 1.41 1.43 1.17 1.30 1.25 1.11 1.51 0.82 1.28 2 1.8 1.6 1.4 1.2 1 Shannon Weiner Index (ave. as of 2004) Shannon Weiner Index (ave. as of 2014) 0.8 0.6 0.4 0.2 Ab or Ar la n a Ba cel la i ba B Br oo ata c ke raz ’s a B Po Ca usu int ga an ya ga nc ill Co o ro Cu n lio n C Du u y m o a El ran Es N id p o Li a ño na la M pa ag c sa an ys ay Na Q rra ue zo n Ri z Sa Ro al n x Vi as ce nt e AV Tay ER ta y AG E 0 28 Tree Density (Number of Trees per Hectare) Of Mangroves by Municipality The Department of Environment and Natural Resources (DENR 1998) categorizes mangrove stocking into the following: adequate stock inadequate stock logged-over – – – 1,500 and above timber size trees per hectare 625 – 1,499 timber size trees per hectare less than 625 trees per hectare Thus, there are municipalities with adequate stock, inadequate stock and logged-over mangrove forests. This is due to continuous human pressure on the mangrove forests which include fishpond development, cuttings for domestic and economic reasons, conversion to settlement areas and other uses. Municipalities Aborlan Araceli Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Culion Cuyo Dumaran El Nido Española Linapacan Magsaysay Narra Quezon Rizal Roxas San Vicente Taytay AVERAGE Average Tree Density as of 2004 1,236 1,372 2,362 591 253 358 2,989 4,910 408 1,323 291 1,415 1,431 2,360 1,171 2,818 131 277 1,428 Average Tree Density as of 2014 1,364 14,164 737 1,546 2,550 72 2,393 4,879 1,458 3,808 1,565 3,331 927 2,730 158 2,779 29 16,000 14,000 12,000 10,000 Average Tree Density as of 2004 8,000 Average Tree Density as of 2014 6,000 4,000 2,000 Ab or la Ar n ac Ba eli la ba B Br oo ata c ke raz ’s a P Bu oi n Ca su t ga ang ya a nc illo Co ro Cu n lio n C Du u yo m ar El an N Es id pa o Li ño na la M pa ag ca sa n ys ay Na Q rra ue zo n Ri za Sa Ro l x n Vi as ce nt T e AV ay ER ta y AG E 0 Average Diameter-at-Breast Height (DBH) Of Mangroves by Municipality The average diameter-at-breast height (dbh) of the mangrove trees in the different municipalities indicate its relative size and can be used to determine the growth rate through time. The table below shows that some of the municipalities manifested an increase in the average diameter-at-breast height while some decrease. The increase is due to the length of time between the baseline assessment and the monitoring which ranges from about 4 to 10 years, thus, the increase in dbh. On the other hand, the decrease may be correlated to the loss of some of the big trees which were recorded in the baseline assessment and not during the monitoring assessment. The loss can be attributed to tree cuttings and clearings for domestic and economic reasons. Municipalities Aborlan Araceli Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Culion Cuyo Dumaran El Nido Española Linapacan Magsaysay Narra Quezon Rizal Roxas Average DBH as of 2004 14.95 11.89 22.80 15.80 13.58 11.30 12.03 16.24 10.33 16.26 11.64 12.09 16.23 15.86 13.44 Average DBH as of 2014 18.25 26.22 17.03 14.17 10.62 19.98 15.47 11.94 12.11 12.39 15.43 33.87 19.05 17.98 30 San Vicente Taytay AVERAGE 11.29 17.03 14.28 18.08 17.51 40 35 30 25 Average DBH as of 2004 20 Average DBH as of 2014 15 10 5 n el i ac Ba or la Ar Ab la ba Br Bat c ar oo ke aza ’s P Bu oin su t C ag ang ay a an ci llo C or on C ul io n C uy D um o ar a El n N Es ido pa Li ñol na a p M aca ag n sa ys ay N ar r Q a ue zo n R iza l Sa Rox as n Vi ce nt e Ta y AV ta ER y AG E 0 Seedling Density (Seedlings per Hectare) Of Mangroves by Municipality Seedling and sapling density are good indicators of the capability of the mangrove forests under human induce stresses for natural regeneration. The tables below show the seedling and sapling densities of the mangrove forests of the different municipalities in the province. Some manifested very high seedling and sapling densities while others are very minimal. High seedling and sapling densities indicate high capacity for natural regeneration. However, this may also mean that these areas are disturbed or have undergone disturbances in the past wherein sunlight penetrate the forest floor favoring the growth and survival of seedlings and saplings. On the other hand, low seedling and sapling densities may indicate that the mangrove forests are relatively intact and the canopies are close. Municipalities Aborlan Araceli Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Culion Cuyo Dumaran Seedling Density as of 2004 57,500 12,994 2,372 5,500 256 4,867 4,005 2,278 Seedling Density as of 2014 1,676 2,104 1,090 852 16,962 91 994 1,879 31 El Nido Española Linapacan Magsaysay Narra Quezon Rizal Roxas San Vicente Taytay AVERAGE 3,958 38,468 170 7,084 23,644 4,620 21,967 3,783 2,169 310 10,886 480 778 378 12,228 15,298 936 976 3781 70,000 60,000 50,000 40,000 Seedling Density as of 2004 Seedling Density as of 2014 30,000 20,000 10,000 Ar Ab or la n a Ba celi la ba Br Ba c oo tar ke az a ’s P Bu oin t s u C ag an ay ga an ci llo C or on C ul io n C uy D um o ar a El n N Es ido pa Li ño na la p M aca ag sa n ys ay N ar Q ra ue zo n R iza l Sa Ro n xas Vi ce nt e Ta y AV ta ER y AG E 0 Sapling Density (Saplings per Hectare) Of Mangroves by Municipality Municipalities Aborlan Araceli Balabac Bataraza Brooke’s Point Busuanga Cagayancillo Coron Culion Cuyo Dumaran El Nido Española Linapacan Magsaysay Narra Quezon Sapling Density as of 2004 2,733 1,231 1,043 5,000 147 1,351 894 1,682 4,384 6,580 129 1,734 6,312 2,775 Sapling Density as of 2011 506 327 293 487 3,976 82 528 893 250 1,077 408 3,344 32 Rizal Roxas San Vicente Taytay AVERAGE 1,410 2,542 1,845 160 2,331 750 223 198 889 7,000 6,000 5,000 4,000 Sapling Density as of 2004 Sapling Density as of 2011 3,000 2,000 1,000 Ab or l Ar a n a Ba cel la i Br Ba ba c oo ta ke raz ’s a Bu Poi n Ca su t ga an ya ga nc ill Co o ro Cu n lio n C Du u yo m a El ran Es N id p o Li a ño na la M pa ag ca sa n ys ay Na Q rra ue zo n Ri za Sa Ro l x n Vi as ce n T te AV ay ER ta y AG E 0 The local government, with the help of the PCSDS, must conduct regular information and education campaign on the importance and other valuable contributions of mangroves, both economically and ecologically, to increase the level of awareness of coastal communities on the importance of coastal resources. The local government must come up with a Municipal Comprehensive Coastal Resource Management Plan that will serve as guide to achieve sustainable development of the coastal areas. Consequently, a detailed water-use plan should be prepared in consonance with the Municipal Comprehensive Land-use Plan (CLUP). Strengthen the protection efforts and law enforcement program of each municipality in the province. The LGU must develop alternative livelihoods for coastal communities to deviate the pressure from the mangrove resources to ecologically-friendly enterprise and other income sources. 33 Seagrass/seaweeds Live Reef Fish Trader shippers and carriers showed declining production from a highest production of 725,647.5kg (725.6475 MT) in 2005 to 384,930 kg (384.930 MT) in 201013 Trader Shippers Carriers 2010 69 Highest # of issued Accreditation in Coron (17), Taytay (10) and San Vicente (6) No issued Accreditation in Linapacan, Magsaysay, Narra and Quezon 13 Highest # of issued Accreditation in San Vicente (4), Taytay (3) and Magsaysay (3) 2011 58 Highest # of issued Accreditation in Taytay (11), Coron (10) and Cuyo (7) No issued Accreditation in Agutaya, Araceli, Busuanga, Cagayancillo, Linapacan, Magsaysay, Narra 17 Highest # of issued Accreditation in Quezon (4), Roxas (3 ) and Magsaysay (3) 13 National and Provincial Policy, Regulation and Enforcement The Palawan Live Reef Food Fish Trade 34 The data is instructive in showing which municipalities has incidence of cyanide use following the DA-BFAR policy of CDT as a monitoring tool for cyanide use Municipality Aborlan Araceli Balabac Bataraza Coron Culion Cuyo No. of Cases in violation of PCSD AO 5, as amended 2 1 2 7 58 1 44 Municipality Narra PPC Quezon Roxas San Vicente Taytay TOTAL No. of Cases in violation of PCSD AO 5, as amended 1 9 4 3 3 6 141 35 • Dominant species • Plectropomus leopardus (Leopard coral trout) • Lesser species – Family Serranidae • P. areolatus (Squaretail coral trout) • P. maculatus (Spotted coral trout) • P. laevis (Blacksaddled coral trout) • P. oligacanthus (Highfin coral trout) • Epinephelus coioides (Orange spotted grouper) • E. malabaricus (Malabar grouper) • E. fuscoguttatus (Brown-marbled grouper) • Cromileptes altivelis (Humpback grouper) (Illegally traded) – Family Panuliridae • Panulirus sp. (Lobster) – Family Labridae (Illegally traded by poachers from other provinces) • Cheilinus undulatus (Napoleon humphead wrasse)14 Live Reef Fish Shipment, Palawan, 2003-2008 800 700 679.3 700.4 640.0 Volume (tons) 600 517.9 500 531.8 400 300 305.2 200 100 0 2002 2003 2004 2005 2006 2007 2008 2009 Year 14 National and Provincial Policy, Regulation and Enforcement The Palawan Live Reef Food Fish Trade 36 Marine Protected Areas (tina) 37 Threats to Coastal and Marine Biodiversity Conversion of habitats (development) Illegal and destructive fishing Overfishing Pollution Climate change The establishment of Marine Protected Areas (MPAs) is promoted as a key tool that can mitigate these threats through the conservation of marine biodiversity, especially for coral reefs Quite a number of these MPAs are scattered throughout Palawan. “These improvements could be largely negated if the predicted threat posed by Global Climate Change of increasing sea surface temperatures and concentrations of CO2 in seawater cause catastrophic bleaching and result in major reductions in the capacity of corals to calcify and grow.”(Wilkinson, 2002) The fundamental principle of building resilience of ecosystems in response to the adverse effects of climatic change is very similar to that used in designing conservation strategies to protect biodiversity from any threat. According to WWF’s Buying time: user’s manual for building resistance and resilience to climate change in natural systems (2003), the strategies are divided into three categories: 1. creation of sufficient space for change 2. reduction of all non-climate stresses 3. identification of resistant and resilient populations for special protection. MPA Network To form a wider space for change, the best solution is often a grouping of smaller MPAs protecting different habitats at various locations within the larger ecosystem to balance the needs of people and the marine environment and to maximize protection benefits that is an ecologically representative network of MPAs. 38 Existing Marine Protected Areas (MPAs) in Palawan Existing Marine Protected Area (MPAs) in Palaw an 120 100 80 60 Total 40 20 0 Existing Proposed 39 Northern Mainland and Island Municipalities Municipality Araceli Dumaran El Nido Roxas San Vicente Taytay Existing 0 0 17 12 4 5 Proposed 0 0 3 0 1 10 Total 0 0 20 12 5 15 Northern Mainland and Island Municipalities 25 20 15 Existing Proposed 10 Total 5 0 Araceli Dumaran El Nido Roxas San Vicente Taytay 40 Calamaianes Group and Notheastern Island Municipalities Municipality Agutaya Busuanga Coron Culion Cuyo Linapacan Magsaysay Existing 2 3 5 4 0 1 0 Proposed 0 0 0 0 0 0 0 Total 2 3 5 4 0 1 0 Calamianes Group and Northeastern Island Municipalities 6 5 4 Existing 3 Proposed Total 2 1 0 Agutaya Busuanga Coron Culion Cuyo Linapacan Magsaysay 41 Southern Mainland and Balabac Municipalities Municipality Aborlan Balabac Bataraza Brooke's Point Narra Quezon Rizal Sofronio Espanola Existing 3 1 1 1 20 2 4 1 Proposed 2 0 0 0 0 0 0 0 Total 5 1 1 1 20 2 4 1 Southern Mainland and Balabac Municipalities 25 20 15 Existing Proposed Total 10 5 0 Aborlan Balabac Bataraza Brooke's Point Narra Quezon Rizal Sofronio Espanola 42 Central Mainland and Caganyancillo Municipality Caganyancillo Puerto Princesa Existing 4 14 Proposed 0 7 Total 4 21 Central Mainland and Caganyancillo 25 20 15 Caganyancillo Puerto Princesa 10 5 0 Existing Proposed Total 43 Protected Coastal and Marine Areas in Palawan Pearl Farm Areas Community-Managed MPAs Large MPAs (NIPAS) Total Area (Has.) 61,369.56**15 44,452.65*16 262,714.00 % to Municipal Waters (4,577,724 has.) 1.34 0.97 5.74 Protected Coastal and Marine Areas in Palaw an 300,000.00 250,000.00 200,000.00 Total Area (Has.) 150,000.00 % to Municipal Waters (4,577,724 has.) 100,000.00 50,000.00 0.00 Pearl Farm Areas CommunityManaged MPAs Large MPAs (NIPAS) Status of Marine Protected Areas (MPAs) in Palawan Municipality Name of Legal Basis of Date Sanctuary Establishment established Total Area (has) Operational (yes/no) Mgt. Plan (y/n) Mgt. Board (y/n) Data gathered shows that there are MPAs that were declared and established but still lack management plans and management boards while some still do not operate. These MPAs have been legally designated on paper, but insufficient resources have not been allocated to implement the strategies for most of them. 15 16 From PCSDS-GIS Partial data 44 Existing Network of Marine Protected Areas (MPAs) in Palawan CCaallaammiiaanneess M Maarriinnee PPrrootteecctteedd AArreeaa N Neettw woorrkk Minugbay-Malbato-Tagpi MPA Bugor-Sand Island MPA Established with the assistance from the Fisheries Improved for Sustainable Harvest (FISH) Project SEC registered for recognition 45 Proposed Network of Marine Protected Areas (MPAs) in Palawan 46 El Nido CommunityManaged Marine Areas Network 11.45 Cagbuli Is Calitan (Bird) Is Nalbot Is 11.40 El Nido, Palawan Diapila (Vilma) Is Brother Is Tiniguiban Daracotan Is Lalutaya Is 11.35 Existing MPA Sites Palakatan Is Bucana Buri Is North latitude (degrees) 11.30 Barotuan San Fernando Sibaltan Caverna Is Bubog Is Caoayan Is 11.25 Pasadena Maapdet Is Miti Is Villa Paz Proposed MPA Sites Inambuyod Is Cadlao Is 11.20 MPA…Subject for enactment of Mun. ordinance but with mgt.plan & brgy.resolution Labnog Is Tapiutan Is Villa Libertad Dilumacad Is New Ibajay EL NIDO Talawtawan Is Matinloc Is 11.15 Corong-corong Tres Marias Miniloc Is North Guntao Is Paglungaban Is Imorigue Is Depeldet Is Entalula Is Cabugao Is Pinagbuyotan Is Pangulasian Is South Guntao Is Mabini Malapacao Is Turtle Is 11.10 Manlag Popolcan Is Mangrove Areas…Subject for enactment of Mun. ordinance but with mgt.plan & brgy.resolution Proposed Mangrove Management Sites Lagen Is Pinasil Is Diboluan Is Aberawan 11.05 Bebeladan Bagong Bayan 11.00 119.25 119.30 On-going Mangrove Management Sites 119.35 119.40 119.45 119.50 119.55 East longitude (degrees) The 102 representative networks of MPAs covering the whole of Palawan, if made into one large network of MPAs, could be the largest in the country. This larger picture as a whole could build resilience to the effects of climate change. If well-designed, the location of MPAs in such a network would allow them to support each other by taking advantage of ocean currents, migration routes, and other natural ecological connections (Davis, 2010). This would help provide much-needed resilience against a range of threats. Management of these MPAs should be sound as to achieve the objectives of each MPA in the network. 47 Pearl Farms To determine through photo documentation the present status of the benthic environment of marine areas in terms of coral reef evaluation under the long lines and within the lease areas of the pearl farms; And, secondly, to determine fish population under the leased areas of the pearl farms. Actual area of sampling areas within the pearl farms. Two or three divers of each pearl farms assist our diver in the establishment of the transect line for the assessment of corals and identification/listing of fishes. Municipality Total Area of Mun. Waters* (ha) Balabac 396,259 Busuanga 194,755 Coron Culion 330,386 100,485 Dumaran 108,222 Linapacan 407,507 San Vicente 149,050 Taytay 292,672 Pearl Farm/Proponent Jewelmer International Corporation Surigao Marine Products, Inc (SUMAPI) Eco-Farm Systems and Resources Inc. Eco-Farm Systems and Resources Inc. Hikari SSP Corporation Hikari SSP Corporation Southern Mineral and Marine Corporation (SOMMACO) Marily Development Corporation Naglayan Pearl Farm Hikari SSP Corporation Port Barton Corporation Sakura Pearl Farm Terramar Pearl Farm Salvamar Pearl Farm Area Occupied by Pearl Farm (leased area in ha)** % Area Occupied by Pearl Farm in municipal waters 8,857.99 2.24 7,791.83 4.00 Total Area (%) Occupied by Pearl Farm in municipal waters 2.24 5.07 2,083.92 1.07 1.51 5,000 575.29 0.17 1.69 2,257 2.25 4,875 4.85 1,408 12,444 1.40 11.50 2,400 0.59 0.00 5,000 5,000 3,676.52 3.35 1.71 1.26 8.5 11.5 0.59 3.35 2.97 *Generated by PCSDS-GIS ** Per PCSDS file 48 Note: R.A.8550, Sec 51… that not over ten percent (10%) of the suitable water surface area of all lakes and rivers shall be allotted for aquaculture purposes. 1.5 Protected Areas The Province of Palawan has the following protected areas: Name of PA Palawan Province Puerto Princesa Underground River Tubbataha Reefs Natural Park Calauit Game Preserve and Wildlife Sanctuary Type and Date of Protection/Inscription Area Proclamation No. 219, s. 1967 (Declaring the Entire Province of Palawan as Game Refuge and Bird Sanctuary, and the Small Islands of Palawan as National Reserves). Entire province Proclamation No. 2152 December 29, 1981 (Declaring the Entire Province of Palawan and Certain Parcels of the Public Domain and/or Parts of the Country as Mangrove Swamp Forest Preserves) Entire province Biosphere Reserve – 1991? Entire province National Park - ___ World Heritage Site- __ Ramsar Site - ____ New Seven Wonders of Nature _____ National Park - ___ World Heritage Site- ___ Ramsar Site - ____ __ Remarks Formerly St. Paul Subterranean River Natl Park Now Calauit Wildlife Park under the Provincial Government Ursula Island Bird Sanctuary El Nido-Taytay Managed Resource Protected Area Malampaya Sound Protected Landscape & Seascape Coron Island 49 Protected Landscape & Seascape Mt. Mantalingahan Protected Landscape Rasa Island Wildlife Sanctuary Others: Palawan Flora, Fauna & Watershed Reserve Palawan Tau’t Bato Reserve? Tabon Caves Complex Reserves? Puerto Princesa Subterranean River National Park Puerto Princesa Subterranean River National Park It is believe to be one of the longest navigable underground rivers in the world which features cathedral-like caverns and domes. The stalactites and stalagmites formation resembles like religious images, fruits and birds. Truly, an admirable underworld that project the omnipotence of the Creator over human hands. The Underground River is home to other cove dwelling fauna. Puerto Princesa Subterranean River National Park was declared by Proclamation No. 835 on March 26, 1971. It is located in the West Coast of Palawan, 81 km north of Puerto Princesa City. 50 The land form in the park are associated with rocky mountains (of marble and limestone) running from north to south. Two-thirds of the area is covered by lush tropical rainforest from the shoreline to the highest peak, and one-third is thinly vegetated karsts limestone. The vegetation types include lowland forest (often with 35 m. canopy), coastal forest and karst forest. Tubbataha Reef National Marine Park17 Designated by UNESCO as World Heritage Site It is home to nearly 400 species of fish and bird species, enough reason to declare Tubbataha as a National Marine Park through Proclamation No. 306 on August 11, 1998 this makes commercial fishing or the collecting of corals illegal within 33,2000 hectares of its reefs and surrounding areas. Tubbataha Reef is located in the middle of the Central Sulu Sea, 98 nautical miles southeast of Puerto Princesa City. It is composed of two large shallow reef platforms enclosing a sandy lagoon. On the seaward portions of the reef platform are steep, often perpendicular reef walls extending to 50 feet. Most of the park area is submereged, with only a few permanent emergent sandy islands. The two atolls are named the North and South Reefs or Islets. The former is a large, oblong-shaped continous reef platform about 4-5 km wide and compeletely encloses a sandy lagoon. The reef is shallow and emergent in some places at extreme low tide. The South Reef likewise is a small triangular-shaped reef about 1-2 km wide . Like the North Reef it consists of a shallow platform enclosing a sandy lagoon. On the souther tip of this reef is a 2-3 ha. Coral line-sand island, the South Islet where the lighthouse stands. This islet is a rookery site for birds and turtles. Tubbataha's trademark among the world divers is its coral walls with extensive colonies of fish. Unfortunately, Tubbataha's pristine and unspoiled nature also attracted not just well wishers but problems as well. As the huge reefs fame has spread worldwide, the number of sports divers visiting it is increasing yearly, adding pressure to the fragile nature of the reefs. 17 http://www.pcsd.ph/protected_areas/tubbataha.htm 51 Calauit Game Preserve and Wildlife Sanctuary The Calauit Game Preserve and Wildlife Sanctuary18 "Home to important Philippine endemic and exotic wildlife from Africa " 18 Calauit Game Preserve and Wildlife Sanctuary (CGPWS) is the Philippines major conservation showcase for wildlife habitat holding the single distinction as the first successful wildlife translocation experiment in Asia. It has evolved to becoming a home of important Philippine endemic and exotic wildlife from Africa The CGPWS was declared by Presidential Proclamation No. 1578 on August 31, 1976. It has total land area of 3,400 hectares with low-lying island in the Calamian group, north of Palawan, It is a short distance from the much larger island of Busuanga. The natural vegetation is lowland forest and mangroves along the coast. Much of the forest has now been replaced by plantations, secondary growth and open grassland. Marine habitat is said to have been haven to the dugong, sea turtles, giant clams, coral reefs and a sanctuary for commercial fish species as well. http://www.pcsd.ph/protected_areas/calauit.htm 52 Calauit achieved its popularity as a unique tourist destination. It has continuously attracted students as well as local and foreign researches who undertake various scientific studies on ecology and wildlife related topics. 1.1.1 Ursula Island Bird Sanctuary Ursula Island Game Refuge and Bird Sanctuary19 19 Ursula Island Game Refuge and Bird Sanctuary was declared through Administrative Order No. 14 on April 30, 1960. The islet of Ursula is approximately 20 kms. Off Brooke's Point in southern Palawan, about one hour by boat from Rio Tuba, Bataraza. http://www.pcsd.ph/protected_areas/ursula.htm 53 The vegetation is made up of old growth lowland forest with moderate undergrowth, consisting mostly of tree saplings and seedlings. Ursula has been promoted in the past as an ecotourism destination, but it is apparently not visited by many tourists at present. Ursula Island is notable for the large concentrations of imperial pigeons that roast there, including numbers of the threatened grey Imperial-pigeons. However, it has been reported that the numbers of pigeons roosting have declined substantially in recent years. Mantanani Scops-owl, a restricted-range small-island specialist, has also been recorded on the island. The shoreline is a migratory and wintering ground for shorebirds and the surrounding waters are valuable feeding grounds for seabirds, particularly terns. The Protected Area Management Board (PAMB) which takes charge of the whole management of the island has ordered a temporary closure of the sanctuary from visitors so as to give time for the birds to recuperate and for the PAMB to adopt necessary measures in order to fully protect the whole island while various exposure activities is on going. El Nido-Taytay Managed Resource Protected Area20 Located in two adjacent municipalities in northern Palawan Mainland, this Protected Area is governed by the precautionary principle, "Sustainable Resource Use and Development that benefits Local Communities." This is to address the threats and pressing problems being faced by the Protected Area like illegal fishing, land conversion, and illegal logging. El Nido -Taytay Managed Resource Protected Area (ENTRMRPA) was proclaimed by virtue of a Presidential Proclamation signed by His Excellency President Joseph Estrada last October 8, 1998 and other proclamations, Department Orders, Republic Acts and Executive Orders, all for the purpose of protecting El Nido. It is one of the eight priority areas of the National Integrated Protected Areas Programme The PA is approximately 90,321 hectares where 36,018 hectares is terrestrial, while 54,303 hectares compose the marine component. The highest peak is at Cadlao Island, with an elevation of 640 meters. The islands and the mainland are dotted with karst limestone formations. There are twenty-one barnagays inside the PA, eighteen barangays from the municipality of El Nido and three from Taytay. The PA is on the western side of the mainland, expanding the boundaries of the former marine reserve. 20 http://www.pcsd.ph/protected_areas/elnido.htm 54 It is governed by the precautionarly principle, "Sustainable Resource Use and Development that benefits Local Communities". This is to address the threats/pressing problems being faced by the PA like illegal fishing, land conversion, illegal logging, etc. The natural resource of El Nido brings benefits to the people of El Nido, the Philippines and the world, but these benefits depend on a healthy environment. To ensure that PA is manage, self-supporting activities were formulated through the setting and collecting of fees from visitors and resource users. The Malampaya Sound Protected Landscape and Seascape21 In the past, the Malampaya Sound is dubbed the ‘Fishbowl of the Philippines.’ Its shoreline is flanked with mangroves and swamps. The waters of the Sound is rich with zooplankton biomass which is suitable for the propagation of the shellfish production for commercial and tourism activities. The protected area is located in the municipality of Taytay. It was proclaimed in July 12, 2000 per Presidential Proclamation # 342 signed by President Joseph E. Estrada. This proclamation was warranted due to it unique, distinct and scientifically significant ecological features. Located at the northwestern part of the Province covering an area of about 200,155 hectares 56% (111,379 has.), the Malampaya Sound and Seascape Protected Area is made up of terrestrial and coastal /marine areas. Thus, it is ecologically and economically important both as a watershed and a rich fishing ground. In the past, it is dubbed as the "Fishbowl of the Philippines" a cliché' that Palawan as a whole is rich in marine resources. It is made up of a number of habitats and eco-systems such as tropical lowland forest, old growth mangroves, coral reefs, sea grass beds and coastal beaches. The area abounds with flora and fauna including species endemic to Palawan. Interestingly, it is also known habitat of the bottle-nosed and Irrawady Dolphins, attesting to its rich biodiversity and uniqueness. 21 http://www.pcsd.ph/protected_areas/malampaya.htm 55 The Sound is divided into two sections namely the Inner and Outer Sounds. Approximately, 13 islands separate the two sections. Its shoreline is flanked with mangroves and swamps. The brackish waters of the Sound is rich with zooplankton biomass and is suitable for the propagation of the shellfish production for commercial purposes and for establishment of tourism industries, national marine parks and reserves. Apparently, the Sound does not only offers significant ecological features but also livelihood opportunities for its surrounding communities More than 156 species of fish are found in the Sound wherein 60 species are considered first class that command high commercial value. Unfortunately however, latest coastal survey results indicated that the coral cover has deteriorated to only 17% live coral cover. This is one reason why the need to protect this fishing ground. Malampaya Sound Protected Land and Seascape covers 22 barnagays, 18 of which are within the political boundary of Taytay and the rest within San Vicente. Seventy percent(70%) of the population are primarily engaged in fishing and secondarily in farming. Others are engaged into agriculture and seaweed culture and fish caging. "Towards a cooperative effort in managing and sustainably developing Malampaya Sound Protected Land and Seascape, respecting the rights of the people, making them aware and enabling them to live progressive lives as a result of well-maintained and life-giving natural resources", is the ultimate vision of the PAMB. The Coron Island Protected Area22 "Towards preserving the cultural heritage vis-à-vis the valuable ecological resource" 22 The main attraction of Coron Island is the series of seven lakes, the most famous of which is the nationally acclaimed cleanest lake in the Philippines, the Kayangan Lake. It also has number of islands with white beaches. The island is inhabited by the Tagbanua indigenous group. http://www.pcsd.ph/protected_areas/coron.htm 56 The island including its surrounding islets was first declared a National Reserve by virtue of Proclamation # 219 on July 2, 1967. In 1978, another proclamation # 1801 declared the island a Tourist Zone and Marine Reserve. This facilitated the transfer of the management to the Philippine Tourism Authority. This proclamation was followed by Proclamation 2152, declaring the entire province a Mangrove Swamp Forest Reserve. Likewise, in 1990, a Community Forest Stewardship Agreement (CFSA) was issued by DENR to the Tagbanua Foundation of Coron Island which covered about 7,748 has. Finally, with the passage of NIPAS Act in 1992, it was listed part of the priority protected areas. Consequently, on June 5, 1998 Coron Island was recognized as an ancestral domain with the issuance of CADC No. 134 to the Tagbanuas. The claim which includes the Tagbanua ancestral fishing grounds, covered 22,248 has., operated via a framework management plan prepared by the aforementioned IP's. Coron Island is wedge-shaped limestone island, dominated by Permian Limestone of Jurassic origin, with few of its coastal areas being covered by mangrove forests. It is situated in the Calamianes group of Islands and belongs to the Municipality of Coron. Aside from being an endemic bird habitat, it is holding distinct assemblages of mammals, reptiles and amphibians. In fact, Coron Island is included in the Palawan Faunal Region. Studies indicated its high rate of floral and faunal endemism. Due to this bio-diverse feature, Coron Island has very high potential for ecotourism. It is one of the priority areas under the sustainable tourism development of Palawan. The main attraction of Coron is the enchantingly situated seven lakes, famous of which is the nationally acclaimed cleanest lake in the Philippines, the Kayangan Lake. It also has number of islands with white beaches, potential for resort developments. However, the once upon a time rich coastal areas of Coron island is constantly facing threats from illegal fishing activities. Today, its coastal resources had dramatically dwindled. Notably , the major stakeholders of the area are the indigenous people named "Tagbanua’s" who represent majority of the settlers. 57 Tabon Caves Complex Mt. Mantalingahan Protected Landscape Mantalingahan is a long mountain range in southern Palawan. The peak of the mountain is the highest point in the province. The protected area status of MMPL was proclaimed last June 23, 2009, by virtue of Presidential Proclamation No. 1815. The protected area covers an area of 120,457 hectares. Continuing discoveries of new species of plant and animal from the mountain highlight its tremendous ecological value and the importance of maintaining this protective area in the face of constant logging and mining pressures. Palawan Flora, Fauna and Watershed Reserve Also known as the Irawan Watershed Reserve, the watershed is the main source of water in the city center and barangays of Puerto Princesa. It is being managed the City Government. Wildlife Flora: Palawan List of Threatened Species FAMILY SCIENTIFIC NAME I. CRITICALLY ENDANGERED SPECIES23 (including those listed under Appendix I of CITES) FLOWERING PLANTS Dipterocarpaceae Dipterocarpus gracilis Dipterocarpaceae Dipterocarpus grandiflorus Dipterocarpaceae Dipterocarpus hasseltii Sapindaceae Guioa palawanica COMMON NAME Panau “Apitong Hasselt Panau II. ENDANGERED SPECIES (including those listed under APPENDIX II & III of CITES) 1. Lauraceae “” Cryptocarya palawanensis Parena 2. Araliaceae Schefflera curranii 3. Araliaceae Schefflera palawanensis 4. Diptocarpaceae Vatica mangachapoi obtusifolia 5. Dipterocarpaceae Vatica maritime 23 Palawan Biosphere Reserve 58 III. VULNERABLE 1. Leguminosae 2. Alangiaceae 3. Euphorbiaceae 4. Euphorbiaceae 5. Meliaceae 6. Myrsinaceae 7. Araliaceae 8. Burseraceae 9. Annonaceae 10. Dilleniaceae 10. Dilleniaceae Meliaceae 13. Celastraceae 14. Leguminosae 15. Myristicaceae 16. Euphorbiaceae 17. Annonaceae 18. Annonaceae 19. Sapotaceae 20. Annonaceae 21. Burseraceae 22. Leguminosae 23. Meliaceae 24. Anacardiaceae 25. Verbenaceae 26. Myrtaceae 27. Flacourtiaceae 28. Rhamnaceae Adenanthera intermedia Alangium longiflorum Antidesma obliquinervium Antidesma subolivaceum Aphanamixis cumingiana Ardisia squamulosa Arthrophyllum pulgarense Canarium luzonicum Dasymaschalon scandens Dillenia luzoniensis Dillenia luzoniensis Dysoxylum palawanensis Glyptopetalum palawanense Intsia bijuga Knema latericia latericia Macaranga cogostiflora Mitrephora fragrans Mitrephora lanota Palaquium bataanense Polyalthia elmeri Protium connarifolium Pterocarpus indicus Sandoricum vidalii Semecarpus paucinervius Vitex parviflora Xanthostemon verdugonianus Xylosma palawanense Ziziphus talanai “Malatanglin” “Malatapai “Tagpo” “Malakatmon” “Ipil” “Lanutan” “Molave” “Mankono” “Porsanbagyo” Balakat Fauna: Palawan List of Threatened Species FAMILY SCIENTIFIC NAME COMMON NAME I. CRITICALLY ENDANGERED SPECIES24 (including those listed under APPENDIX I of CITES) A. BIRDS: Psittacidae Cacatua haematuropygia Philippine Cockatoo 1 Falconidae Falco peregrinus Peregrine Falcon Phasianidae Polyplectron emphanum1 Palawan Peacock Pheasant Columbidae Caloenas nicobarica1 Nicobar Pigeon B. REPTILES 24 Palawan Biosphere Reserve 59 Cheloniidae 2. Bataguridae 3. Crocodylidae 4. Crocodylidae 5. Cheloniidae 6. Cheloniidae 7. Cheloniidae 8. Dermocheliidae C. MAMMALS Dungongidae Cervidae Phocoenidae Balaenopteridae Balaenopteridae Balaenopteridae Balaenopteridae Eretmochelys imbricata Seibenrockeilla leytensis Crocodylus mindorensis Crocodylus porosus1 Chelonia mydas1 Lepidochelys olivacea1 Caretta caretta1 Dermochelys coriacea1 Hawksbill Turtle Philippine Pond Turtle Philippine Crocodile Saltwater Crocodile Green Turtle Olive Ridley Turtle Loggerhead Turtle Leatherback Turtle Dugong dugon1 Axis calamianensis1 Neophocaena phocaenoides1 Balaenoptere edeni1 Balaenoptera acutorostrata1 Megaptere novaeangliae1 Physeter macrocephalus1 Seacow Calamian Hog Deer Finless Porpoise Bryde’s Whale Minke Whale Humpback Whale Sperm Whale II. ENDANGERED SPECIES (including those listed under APPENDIX II & III of CITES) A. BIRDS Ardeidae Gorsachius goisagi1 Japanese Night Heron Ardeidae Tringa guttifer Nordmann’s Greenshank Megapodiidae Megapodius cumingii2 Tabon Scrubfowl Accipitridae Aviceda jerdoni3 Jerdon’s Baza,/ Crested LizardHawk 3 Accipitridae Pernis ptilorhyncus Asiatic Honeybuzzard Accipitridae Milvus migrans3 Black Kite Accipitridae Haliastur indus3 Brahminy Kite Accipitridae Haliaeetus leucogaster3 White-bellied Sea Eagle 3 Accipitridae Spilornis cheela Crested Serpent Eagle Accipitridae Circus spilonotus3 Eastern Marsh-Harrier 11. Accipitridae Accipiter gularis3 Japanese Sparrow Hawk 3 12. Accipitridae Accipiter trivirgatus Crested Goshawk 13. Accipitridae Accipiter soloensis3 Chinese Goshawk 14. Accipitridae Butastur indicus3 Grey-faced Buzzard 15. Accipitridae Spizaetus cirrhatus3 Changeable Hawk-Eagle 3 16. Accipitridae Spizaetus philippensis Philippine Hawk Eagle 17. Pandionidae Pandion haliaetus3 Osprey 18. Falconidae Falco tinnunculus3 Eurasian Kestrel 3 19. Falconidae Falco severus Oriental Hobby 20. Psittacidae Prioniturus platenae3 Blue-headed Racquet Tail . Psittacidae Tanygnathus lucionensis3 Blue-naped Parrot 22. Strigidae Otus mantananensis3 Mantanani Scops Owl 3 23. Strigidae Otus fuliginosus Palawan Scops Owl 24. Strigidae Ninox scutulata3 Brown Hawk-Owl 25. Strigidae Strix seloputo3 Spotted Wood Owl 3 26. Strigidae Asio flammeus Short-Eared Owl 27. Bucerotidae Anthracoceros marchei3 Palawan Hornbill 28. Sturnidae Gracula religiosa palawanensis3 Palawan Mynah 60 B. REPTILES 1. Trionychidae 2. Varanidae 3. Boidae 4. Elapidae 5. Elapidae C. MAMMALS 1. Sciuridae 2. Muridae Pelochelys cantorii Varanus salvator3 Python reticulates3 Ophiophagus hannah3 Naja naja3 Cantor’s Giant Softshell Variable Monitor Lizard Reticulated Python King Cobra Asiatic Cobra Sundasciurus juvencus Palawanomys furvus 3. Tragulidae Tragulus napu nigricans 4. Balaenopteridae 5. Manidae 6. Felidae 7. Mustelidae 8. Cercopithecidae 9. Tupaiidae 10. Pteropodidae 11. Pteropodidae 12. Delphinidae 13. Delphinidae 14. Delphinidae 15. Delphinidae 16. Delphinidae Balaenoptera physalus Manis culionensis3 Prionailurus bengalensis3 Amblonyx cinereus3 Macaca fascicularis3 Tupaia palawanensis3 Pteropus vampyrus3 Acerodon leucotis3 Tursiops truncatus3 Lagenodelphis hosei3 Stenella attenuata3 Grampus griseus3 Stenella longirostris3 17. Delphinidae D. CLAMS 1. Tridacnidae 2. Tridacnidae FISH 1. Labridae Globicephala macrorhyncus3 Northern Palawan Tree Squirrel Palawan Soft-furred Mountain Rat Balabac Chevrotain, Mousedeer Fin Whale Palawan Pangolin Leopard Cat Oriental Small-clawed Otter Long-tailed Macaque Palawan Tree Shrew Large Flying Fox Palawan Flying Fox Bottlenosed Dolphin Fraser’s Dolphin Pantropical Spotted Dolphin Risso’s Dolphin Long-snouted Spinner Dolphin Short-finned Pilot Whale Hippopus hippopus3 Hippopus porcelanus3 Bear’s Paw Clam China Clam Cheilinus undulatus Napoleon Fish/Humphead Wrasse III. VULNERABLE A. BIRDS B. MAMMALS C. AMPHIBIANS 61 D. MARINE FISH E. FRESHWATER FISH F. CLAMS IV. OTHER THREATENED SPECIES (NEAR THREATENED SPECIES) A.BIRDS B.MAMMALS C.REPTILES PUT THE BELOW LIST IN THE TABLE III. VULNERABLE FAMILY A. BIRDS 1. Ardeidae 2. Columbidae 3. Muscicapidae 4. Muscicapidae 5. Scolopacidae SCIENTIFIC NAME Egretta eulophotes Ducula pickeringii Ptilocichla falcate Ficedula platenae Numenius tahitiensis COMMON NAME Chinese Egret Grey Imperial Pigeon Falcated Ground-babbler Palawan Flycatcher Bristle-thighed Curlew 62 B. MAMMALS 1. Soricidae Crocidura palawanensis 2. Sciuridae Sundasciurus rabori 3. Mustelidae Mydaus marchei 4. Viverridae Arctictis binturong whitei 5. Suidae Sus barbatus ahoenobarbus Palawan Shrew Palawan Montane Squirrel Palawan Stink Badger Palawan Bearcat Palawan Bearded Pig C. AMPHIBIANS 1. Discoglossidae 2. Bufonidae 3. Ranidae Philippine Discoglossid Frog Palawan Toadlet Mary Inger’s Frog Barbourula busuangensis Pelophryne albotaeniata Ingerana mariae D. MARINE FISH 1. Serranidae Epinephelus lanceolatus 2. Rhincodinidae Rhincodon typus 3. Ginglymostomatidae Nebrius ferrugineus 4. Rhynchobatidae Rhyncobatus djiddensis 5. Stegostomatidae Stegostoma fasciatum Giant Grouper Whaleshark Tawny Nurse Shark White-spot Giant Guitarfish Leopard Shark E. FRESHWATER FISH 1. Cyprinidae Puntius manguaoensis Lake Manguao Barb F. CLAMS 1. Tridacnidae 2. Tridacnidae Smooth Giant Clam Giant Clam Tridacna derasa Tridacna gigas IV. OTHER THREATENED SPECIES (NEAR THREATENED SPECIES) FAMILY SCIENTIFIC NAME COMMON NAME A. BIRDS 1. Charadriidae 2. Timaliidae 3. Timaliidae 4. Muscicapidae 5. Muscicapidae 6. Muscicapidae 7. Paridae Charadrius peronii Malacopteron palawanens? Stachyris hypogrammica Cyornis lemprieri? Tersiphone atrocaudata Tersiphone cyanescens Parus amabilis Malaysian Plover Melodius Babbler Palawan Striped-Babbler Palawan Blue Flycatcher Japanese Paradise Flycatcher Blue Paradise-Flycatcher Palawan Tit B. MAMMALS 1. Muridae 2. Sciuridae 3. Muridae Maxomys panglima Sundasciurus moellendorffi Hylopetes nigripes Palawan Spiny Rat Culion Tree Squirrel Palawan Flying Squirrel C. REPTILES 1. Emydidae Cuora amboinensis South Asian Box Turtle Notes: 1 CITES-Listed, Appendix I 2 Species declared as Endangered in Palawan by virtue of PCSD Resolution No. 93-22 3 CITES-Listed, Appendix II 63 Invasive Alien Species 64