of the Verde Island Passage, Philippines - weADAPT
of the Verde Island Passage, Philippines - weADAPT
of the Verde Island Passage, Philippines - weADAPT
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chapter 1 • vulnerability assessment <strong>of</strong> marine ecosystems and fisheries to climate change: vulnerability<br />
Table 22. Vulnerability assessment <strong>of</strong> <strong>the</strong> fisheries based on number <strong>of</strong> gear types per habitat type.<br />
Habitat type<br />
Caught by sand/ estuarine Vulnerability<br />
Species/taxa gear type reef beach mangrove seagrass creeks/rivers pelagic index<br />
Mabini, Batangas<br />
dulong (Spratelloides)<br />
dilis (Engraulis)<br />
alumahan (Rastrelliger)<br />
tambakol (Katsuwonus)<br />
galunggong (Decapterus)<br />
matambaka (Selar)<br />
lapu-lapu (groupers)<br />
maya-maya (Lutjanus)<br />
kanoping (Lethrinus)<br />
bisugo (nemipterids)<br />
tulingan (Auxis)<br />
pusit (Sepioteuthis, Loligo)<br />
No. <strong>of</strong> gears per habitat<br />
Level <strong>of</strong> fishing effort<br />
<strong>Verde</strong> <strong>Island</strong>, Batangas City<br />
angelfish (Pomacanthus)<br />
butterflyfish (Chaetodontus)<br />
damselfish (Chromis)<br />
anthiinid (Anthias)<br />
lion fish (Pterois)<br />
lapu-lapu (groupers)<br />
manites (Upeneus)<br />
galunggong (Decapterus)<br />
alumahan (Rastrelliger)<br />
dalagang bukid (Caesio)<br />
mulmol (Scarus)<br />
labahita (Naso)<br />
pusit (Sepioteuthis, Loligo)<br />
No. <strong>of</strong> gears per habitat<br />
Level <strong>of</strong> fishing effort<br />
basnig (bag net), lambat<br />
pandulong (gill net), scissor net<br />
lambat pante (gill net)<br />
lambat pante (gill net)<br />
hayhay (surface long line)<br />
hayhay (surface long line)<br />
lambat pante (gill net)<br />
kawil (hook and line), pana (spear)<br />
hayhay (surface long line)<br />
pamanos (squid jig)<br />
hand nets (barrier net)<br />
kawil (hook and line)<br />
hayhay (long line)<br />
lambat (gill net)<br />
pana (spear)<br />
pamanos (squid jig)<br />
1<br />
2<br />
1<br />
4 (high)<br />
medium<br />
to high<br />
1<br />
1<br />
1<br />
1<br />
1<br />
1<br />
6 (high)<br />
medium<br />
1<br />
1 (low)<br />
low<br />
1<br />
1 (low)<br />
low<br />
1<br />
1 (low)<br />
low to<br />
medium<br />
1<br />
1<br />
2 (medium)<br />
medium<br />
4<br />
1<br />
5 (high)<br />
medium<br />
to high<br />
1<br />
1<br />
2 (medium)<br />
medium<br />
medium to high<br />
medium<br />
Table 23. Matrix <strong>of</strong> prospective responses to climate change impacts highlighting <strong>the</strong> interacting effects between habitats and fisheries.<br />
Responses<br />
Climate<br />
estuaries/<br />
change impact seagrass seaweeds reef fish mangroves creeks/rivers pelagic groupers<br />
increased sea<br />
surface<br />
temperature<br />
can be approached<br />
similar to corals/diversity<br />
<strong>of</strong> associated organisms;<br />
associated fishereies, e.g.,<br />
siganids, and high value<br />
invertebrate fisheries,<br />
reduced catch in some<br />
finfish but may have a<br />
shift to detritivores and<br />
omnivores<br />
phenological<br />
characteristic disrupted;<br />
change in overall<br />
community structure;<br />
slower growth and lower<br />
diversity; low fecundity <strong>of</strong><br />
species<br />
reproductive output,<br />
timing, survivorship <strong>of</strong><br />
recruits; recruitment lag/<br />
failure; shorter larval<br />
duration; abundance <strong>of</strong><br />
coral dependent species<br />
will be reduced following<br />
coral bleaching events<br />
and decreased structural<br />
complexity<br />
decreased seedling<br />
production, survivorship<br />
and recruitment; lower<br />
recruitment regeneration;<br />
phenological<br />
characteristics disrupted;<br />
associated fisheries<br />
will be reduced for<br />
temperature dependent<br />
reproductive output<br />
see mangroves and<br />
associated fisheries<br />
especially in relation to<br />
ontogenetic habitats<br />
shifts and how adjacent<br />
habitats can be seen in<br />
exacerbated/synergistic<br />
negative effects,<br />
overfishing, and habitat<br />
fragmentation/loss<br />
shorter larval duration;<br />
decreases survivorship<br />
due to low food<br />
availability; alter<br />
reproductive periodicity<br />
and eventual recruitment<br />
survivorship leading<br />
changes in fisheries<br />
productivity<br />
shorter larval duration;<br />
enhanced recruitment<br />
variability; recruitment<br />
will be affected following<br />
decreased structural<br />
complexity via coral<br />
bleaching ;<br />
reproductive output and<br />
timing <strong>of</strong> reproduction will<br />
be affected, especially<br />
spawning aggregations<br />
sea level rise<br />
shallow species will be<br />
most sensitive to change<br />
and will be vulnerable;<br />
species found growing on<br />
<strong>the</strong> slopes can adjust to<br />
changing depth<br />
can be well adapted to<br />
changes in sea levels<br />
(community level/change<br />
in community structure)<br />
inundation <strong>of</strong> mangroves<br />
and associated species<br />
(fauna); reduce conditions<br />
for settlement availability<br />
as nursery grounds for<br />
o<strong>the</strong>r species; change in<br />
sedimentation dynamics;<br />
substrate erosion<br />
increase storm<br />
intensity and<br />
frequency<br />
• storm paths/<br />
tracks<br />
• storm surge<br />
disrupt recruitment events<br />
<strong>of</strong> associated faunal<br />
species; decreases<br />
survivorship<br />
change in substrate<br />
composition leading<br />
to changes in algal<br />
community structure;<br />
burial and scouring<br />
topographic complexity/<br />
habitat refuge<br />
(composition, biomass,<br />
density); this can lead<br />
to reduced fisheries<br />
productivity<br />
disrupt recruitment events<br />
<strong>of</strong> associated faunal<br />
species (e.g., groupers,<br />
snappers, jacks);<br />
decreases survivorship<br />
propagules dislodged<br />
prematurely; uprooting<br />
<strong>of</strong> mature trees along<br />
shoreline<br />
decreases survivorship<br />
<strong>of</strong> recently recruited<br />
associated faunal species<br />
(e.g., groupers, snappers,<br />
sprats, anchovies, bangus<br />
fry)<br />
affect recruitment due to<br />
loss <strong>of</strong> habitat availability<br />
for settlement (e.g.,<br />
decresed structural<br />
complexity)<br />
rainfall<br />
• changes in<br />
salinity<br />
• increased<br />
sedimentation<br />
change in water quality<br />
will have changes in light<br />
requirements/availability<br />
only a few species are<br />
stenohalines species that<br />
can survive<br />
burial and mortality<br />
can lead to habitat<br />
modification and reduce<br />
diversity and abundance;<br />
this reduces fisheries<br />
production<br />
have salinity regulatory<br />
function<br />
change in sedimentation<br />
dynamics<br />
affect recruitment<br />
<strong>of</strong> associated faunal<br />
species; decreases <strong>the</strong>ir<br />
survivorship<br />
nutrient increases may<br />
lead to blooms<br />
ocean<br />
acidification<br />
will increase CO 2<br />
;<br />
may favor seagrass<br />
photosyn<strong>the</strong>sis but may<br />
not happen if <strong>the</strong> system<br />
is already distressed<br />
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