୯ҥᆵεᏢᏢଣੇࢩࣴز܌
ᅺγፕЎ
Institute of Oceanography College of Science
National Taiwan University Master Thesis
ѠڬൎੇୱΓπങᕛങᜪဂᆫ่ᄬϐ
A Study on the Structure of Fish Communities around Artificial Reefs in the Coastal Waters of Taiwan
݅ځᑉ Chi-Ying Lin
ࡰᏤ௲Ǻ၏ᄪਦ റγǵᔎܱስ റγ
Advisor: Rong-Quen Jan, Ph.D., Chang-Feng Dai, Ph.D.
ύ҇୯ 100 ԃ 7 Д
July, 2011
ᖴᜏ
ሤӀबǴٿԃޑᅺγғఱǴӧ೭ጇፕЎޑֹԋࡕΨջஒࢤပǶ२ӃǴ ךाགᖴࡰᏤ௲၏ᄪਦԴৣӧᏢ႐ಒᜧᒪޑࡰᏤǵှൽǴаϷӧғࢲค
༾όԿޑᜢྣǹӕਔǴΨाགᖴੇࣴ܌ޑࡰᏤ௲ᔎܱስԴৣǴӧᏢғፕЎቪբ ය໔ǴόჇځྠޑঅ҅ךᒱᇤޑᢀۺаϷಉЈԋޑᇤǶќѦǴഋ҅ѳԴৣᆶ ഋ҅૧Դৣӧα၂๏ϒךӭᝊޑཀـǴᡣךख़ཥࡘԵচҁ۹ౣޑಒǴ٬
ளҁጇፕЎளаճֹԋǶ
ԜѦǴךΨाགᖴഉՔךٿԃਔӀޑύࣴଣჴᡍ࠻ޑუՔॺǺܮܮǵε൬ǵ
ࡹᏢߏǵࡌᏢߏǵӀǵܴ፣ǵە⪭ǴаϷ܌ჴᡍ࠻ޑᗦᏢߏǵ݇Ꮲ ߏǵԖᏢߏǵߙયǵስ൛ǵᅺЎǴགᖴεৎӧፕЎБय़ගٮӭᡍکࡰᏤǴ ӧВதғࢲύޑϩ٦ᆶᜢᚶǴΨ٬ך७གྕធǶ
ךᗋाགᖴࢅ๔کγѶǴதᡣךѦഁѦ௦ኬǴࣁךޑࣴزғғఱᓎబӭ
፪ᆶઢǹӧѠчޑεᏢӕᏢॺঁДޑᓓ௶ҬࢬǴᡣךԖΚᝩុᆶךޑኧ ᏵᏟରǹדᆶЎᅴǴԛӣଯкႝਔගٮךՐ܌ǴᗋததъڹѺႝ၉ћךଆ
᠐ਜǵቪፕЎǴᗋԖӭܻ϶ޑᜢЈᆶႴᓰǴᡣךளа୲ոΚֹԋҞǴӧ ԜǴٳठคКޑགᖴǶ
നࡕǴךाགᖴךޑР҆ߏΦаٰޑЍᆶคค৷ޑбрǴᡣߏԃӧѦ
ᏢޑךૈғࢲคဤǴරҞ߿۳ᏟǶᙣᙖԜፕЎǴ๏ךനᒃངޑݿݿ༰༰Ǵ کךӅ٦೭ҽ഻৹Ƕ
݅ځᑉ ᙣठܭ ѠεᏢ ੇࢩࣴز܌ ύ҇୯ 100 ԃ 8 Д
ᄔा
ࣁΑػၗྍǵቚуᅕᕇǴѠڬൎੇୱԾ҇୯ 60 ԃжଆ໒ۈՉΓπങᕛ ޑǶߏයаٰǴᗨฅςഌុԏΑӭങᕛޑങᜪဂᆫၗǴόၸჹΓ πങᕛങᜪၗྍػޑᐒڋᆶ܌ڙޑज़ڋǴ٠όࢂࡐమཱǶӧԾฅᕉნύǴങᜪ ޑဂᆫ่ᄬӭڙډғނ܄کߚғނ܄ޑᕉნӢη܌ቹៜǴԶങᜪޑ१܄ಔԋ߾ё ϸࢀғᄊᡏسύޑૈໆٮ๏ϷځሀǴҁΓπങᕛങᜪဂᆫޑϩǴΨ
ࢂ୷ܭԜཷۺǶԏ 2008-2010 ԃӧѠڬൎΓπങᕛჴӦወНፓ܌ฦᒵ ޑങᜪဂᆫǵۭғނ࣬ᆶᕉნӢηၗǴӅ 135 Ǵၸങᜪဂᆫ่ᄬǵғނ ဂᆫࡰǵᕴ׀ኧᆶғނໆޑϩǴᡉҢΓπങᕛޑങᜪဂᆫܴᡉё٩Ӧ
ޑৡ౦ϩԋ 4 ঁϩЍǴԶᕛࠠޑቹៜ߾ၨλǶBIO-ENV ᆶ௨ׇϩ่݀ᡉҢǴ
ᡏԶقǴёૈቹៜങᜪဂᆫޑӢηࣁጎࡋǵૈـࡋǵۭ፦ᜪࠠǵ؇ᑈނࠆࡋǵᝯ ᜪᙟᇂᆶᕴғނᙟᇂǴځύߚғނ܄ޑᕉნӢηᆶങᜪဂᆫޑ࣬ᜢ܄ၨଯǶ १܄ಔԋϩᡉҢǺаᕴғނໆԶقǴΓπങᕛύаឪ१คૉނޑങᜪ՞
നӭǹќѦǴՋࠄੇୱᕛޑλࠠങᜪኧໆᙦǴӢԜϣҭӭ१ങ܄ങᜪǹᚆ
ᕛ߾ӭឪ१ੌෞނޑങᜪǹܿࠄϷᚆᕛᝯᜪᙟᇂၨଯǴᝯ१܄ങᜪ
܌՞ޑКٯҭၨଯǶऩағނໆࡰǴчങᕛޑᅕၗྍаΟጕᚊങ (Parapristipoma trilineatum)ǵҡඬങ (Epinephelus lanceolatus)ǵచҡ᜶
(Oplegnathus fasciatus) ՞ᓬ༈ǹՋࠄࣁሌદಂ᜶ (Lutjanus argentimaculatus)ǵൂ
ඬಂ᜶ (Lutjanus monostigma) ᆶ೬য (Plectorhinchus cinctus)ǹܿࠄࣁᒯ׀᜶
(Prionurus scalprum) ᆶѤᚊങ (Pomadasys quadrilineatus)ǹᚆࣁӾવᐪങ (Platax teira) ᆶϤሷങ (Naso hexacanthus)ǶᏃᆅчǵՋࠄᕛങᅿᙦࡋό ऩܿࠄᆶᚆǴՠჹܭᔮ܄ങᅿၗྍޑػǴࠅၨܿࠄᆶᚆܴᡉǶ
ᜢᗖӷǺΓπങᕛǹങᜪဂᆫǹ१܄ಔԋ
Abstract
Artificial reefs (ARs) have been deployed in the coastal waters of Taiwan for fisheries enhancement since the 1970s. Information on fish communities around ARs has been available for many AR sites. However, we still don’t have enough knowledge on mechanisms accounting for the resource enhancement and the limitations of the AR application. In a natural environment, fish communities are opted to be affected by both biological and non-biological environmental factors. And the trophic composition of the organisms basically implies the supply of energy and its transfer in an ecosystem.
Stemmed from these perceptions, the present study has launched a wide spectrum of analysis on fish communities. Data of fish assemblages collected during 2008-2010 from 135 AR sites by scuba divers in waters around Taiwan, along with data of epibenthic cover and environmental factors, were used for analyses on community characteristics, fish abundance and fish biomass. Dendrograms from cluster analysis showed 4 clear clusters of fish assemblages, which could be attributed to geographical areas. In contrast, the effect of AR types was less evident. BIO-ENV and ordination analysis revealed that the structure of overall fish communities were affected more by latitude, water transparency, substratum type, sedimentation, algal coverage and total live cover. Non-biological factors apparently predominated over biotic factors. Trophic analysis showed that invertebrate feeders were common at most AR sites. Besides, in southwestern waters, with the abundant cardinal fishes and damselfishes, a higher proportion of carnivores and piscivores occurred. At offshore islands, planktivores predominated. In both southeastern waters and offshore islands, higher biomasses of herbivores occurred in parallel to higher algal coverages in these regions. Using biomass as an indicator, Parapristipoma trilineatum, Epinephelus lanceolatus and
Oplegnathus fasciatus were regarded as the major fishery resource for the AR sites in northern waters; Lutjanus argentimaculatus, L. monostigma and Plectorhinchus cinctus in southwestern waters; Prionurus scalprum and Pomadasys quadrilineatus in
southeastern waters; and Platax teira and Naso hexacanthus at offshore islands. Overall, ARs deployed in northern and southwestern waters were more effective in terms of enhancing the production of economically important fishes when compared with those in other waters, despite that the fish assemblages there were less diverse.
Key words: artificial reef; fish community; trophic structure
Ҟᒵ
ᖴᜏǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ύЎᄔाǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ मЎᄔाǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ҞᒵǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ კҞᒵǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ߄ҞᒵǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ
൘ǵقǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 1.1 ΓπങᕛޑۓကᆶфૈǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 1.2 ΓπങᕛޑᆫങচǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 1.3 ቹៜΓπങᕛങᜪဂᆫޑӢηǸǸǸǸǸǸǸǸǸǸǸǸǸ 1.4 ങᜪဂᆫᆶ१܄ಔԋǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 1.5 ߈යѠΓπങᕛങᜪဂᆫ࣬ᜢࣴزǸǸǸǸǸǸǸǸǸǸ 1.6 ࣴزҞޑǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ມǵБݤǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 2.1 ၗٰྍǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 2.2 ࣴزኬǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 2.3 ፓБݤǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ
I II III
V VII VIII
1
1
1
2
4
5
5
7
7
7
7
2.4 ၗϩǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ
ୖǵ่݀ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 3.1 ങᜪဂᆫϩǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 3.2 ӦᆶᕛࠠϩǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 3.3 ᕉნӢηЬԋϩϩǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 3.4 ᕉნӢηᆶങᅿಔԋᜢ߯ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 3.5 ௨ׇϩǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 3.6 १܄ಔԋϩǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ စǵፕǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 4.1 ΓπങᕛܫޑՏᆶങᜪဂᆫ่ᄬǸǸǸǸǸǸǸǸǸ 4.2 όӕᕛࠠჹങᜪဂᆫޑቹៜǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 4.3 ങᜪဂᆫϩѲᆶᕉნӢηᜢ߯ǸǸǸǸǸǸǸǸǸǸǸǸǸ 4.4 ങᜪဂᆫᆶ१܄ಔԋǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ 4.5 ่ፕǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ҴǵୖԵЎǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ഌǵკǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ࢠǵ߄ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ
8
14
14
14
16
17
17
19
21
21
22
24
26
27
29
39
51
კҞᒵ
კ 1. Ѡڬൎੇୱ 135 ০ΓπങᕛෳઠޑϩѲՏǸǸǸǸǸǸǸǸǸǸǸǸ კ 2. Ѡڬൎੇୱ 135 ০Γπങᕛෳઠങᜪဂᆫ่ᄬޑဂϩ่݀ǸǸǸ კ 3. Ѡڬൎੇୱ 135 ০Γπങᕛෳઠޑങᜪဂᆫ MDS ϩ่݀ǸǸǸǸǸ კ 4. ѠڬൎੇୱѤঁϩޑΓπങᕛෳઠ໔ޑങᜪဂᆫࡰКၨǸǸǸǸ კ 5. ѠڬൎੇୱѤঁϩޑΓπങᕛෳઠ໔ޑങᜪᕴ׀ኧᆶғނໆКၨǸ კ 6. ѠڬൎੇୱӚϩύόӕᕛࠠޑΓπങᕛෳઠങᜪᕴ׀ኧϷғނໆ
КၨǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ კ 7. Ѡڬൎੇୱ 135 ০Γπങᕛෳઠύ 12 ᅿۭғނᙟᇂޑЬԋϩϩ
კǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ კ 8. ୷ܭკ 7 ޑϩ่݀ǴࡷᒧрΓπങᕛෳઠύၨᡉޑғނ܄ᕉნӢη
ᆶߚғނ܄ᕉნӢηޑЬԋϩϩკǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ კ 9. Ѡڬൎੇୱ 135 ০ΓπങᕛෳઠᆶᕉნᡂኧϐڂࠠჹᔈϩᚈׇკǸ კ 10. Ѡڬൎੇୱ 135 ঁෳઠϐ 18 ᅿж߄܄ങᅿǵ135 ঁෳઠᆶᕉნᡂኧ
ϐڂࠠჹᔈϩΟׇკǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ კ 11. ѠчΓπങᕛޑж߄܄ങᅿᆶᕉნᡂኧϐϧᎩϩᚈׇკǸǸǸǸ კ 12. ѠՋࠄΓπങᕛޑж߄܄ങᅿᆶᕉნᡂኧϐϧᎩϩᚈׇკǸǸǸǸ კ 13. ѠܿࠄΓπങᕛޑж߄܄ങᅿᆶᕉნᡂኧϐϧᎩϩᚈׇკǸǸǸǸǸ კ 14. ѠڬൎᚆΓπങᕛޑж߄܄ങᅿᆶᕉნᡂኧϐϧᎩϩᚈׇკǸǸ
39 40 41 42 42
43
44
44 45
46 47 48 49 50
߄Ҟᒵ
߄ 1. ҁࣴز܌٬ҔޑኧᏵ܌఼ᇂޑΓπങᕛϷځᕛࠠᆶኧໆǸǸǸǸǸǸ ߄ 2. ѠڬൎੇୱόӕӦޑΓπങᕛങᜪဂᆫಔԋ SIMPER ϩ่݀Ǹ ߄ 3. ܿࠄΓπങᕛόӕᕛࠠങᜪဂᆫৡ౦ଛჹϩ่݀ǸǸǸǸǸǸǸǸ ߄ 4. ᚆΓπങᕛόӕᕛࠠങᜪဂᆫৡ౦ଛჹϩ่݀ǸǸǸǸǸǸǸǸ ߄ 5. ѠڬൎੇୱѤঁΓπങᕛނᅿᙦࡋࡰ (D)ǵӭኬ܄ࡰ (H’)
ᆶ֡Ϭࡋࡰ (J’) ޑᡂ౦ኧϩ่݀ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ߄ 6. ѠڬൎੇୱٿٿΓπങᕛނᅿᙦࡋࡰ (D)ǵӭኬ܄ࡰ (H’)
ᆶ֡Ϭࡋࡰ (J’) ޑ Mann-Whitney Test ᔠۓ่݀ǸǸǸǸǸǸǸǸǸ ߄ 7. ѠڬൎੇୱΓπങᕛӧѤঁӦϩΠǴόӕᕛࠠނᅿᙦࡋࡰ
(D)ǵӭኬ܄ࡰ (H’) ᆶ֡Ϭࡋࡰ (J’) ޑᡂ౦ኧϩ่݀ǸǸǸǸǸ ߄ 8. ѠڬൎੇୱѤঁΓπങᕛങᜪᕴ׀ኧᆶғނໆޑᡂ౦ኧϩ่݀Ǹ ߄ 9. ѠڬൎੇୱٿٿΓπങᕛങᜪᕴ׀ኧᆶғނໆޑ Mann-Whitney
Testᔠۓ่݀ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ߄ 10. ѠڬൎੇୱΓπങᕛӧѤঁӦϩΠǴόӕᕛࠠങᜪᕴ׀ኧᆶғ
ނໆޑᡂ౦ኧϩ่݀ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ߄ 11. ਥᏵ߄ 10 ϐϩ่݀Ǵа Mann-Whitney Test ჹԖᡉৡ౦ޑ
ӢηՉόӕᕛࠠଛჹКၨޑ่݀ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ߄ 12. Ѡڬൎੇୱ 135 ০Γπങᕛύങᜪဂᆫᆶᕉნᡂኧޑ BIO-ENV ϩ
่݀ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ߄ 13. ճҔ SIMPER ϩ௨рѠڬൎੇୱόӕΓπങᕛޑж߄܄ങᅿǸǸ ߄ 14. ߄ 13 ϐѠڬൎੇୱѤঁӦϩύޑ߄܄ങᅿǴځ܌ឦᕛᕉნᡂ
ኧᆾӦьᛥᡉ܄ᔠᡍޑ่݀ǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸǸ ߄ 15. ѠڬൎੇୱόӕӦϩΓπങᕛޑᜪ१܄ಔԋǸǸǸǸǸǸǸǸǸ
51 52 52 52
53
53
54 55
55
56
57
58 59
60 61
൘ǵق
1.1 Γπങᕛޑۓကᆶфૈ
ȨΓπങᕛȩࡰޑࢂԖҞޑӦܫӧੇԾฅ፦܈Γޑ่ᄬނᡏǴ
ၸੇނϯϷғᄊޑբҔΠǴૈኳᔕр٤Ϻฅᕛޑ܄Ǵᙖаׯ๓܈ӆੇࢩ ғނޑ܌Ǵػੇࢩғނၗྍ (Jensen et al. 2000; Seaman and Jensen 2000)Ƕݢ ༧ǵዸᓐǵँǵੇᢕݨѳѠΓ่ᄬނΨதੇࢩғނ܌ߕǴՠځ٠ߚ ၀ࡼޑЬाҞޑǴӧၨᝄᙣޑۓကΠǴхࡴཀѦ؈ؒޑಭଫǴᗨฅΨૈ
ගٮ܌ޑфૈǴᔈ၀௨ନӧΓπങᕛϐѦ (Guerin 2009)Ƕ
Γπങᕛന߃ޑҞޑࢂ׆ఈૈගଯݮ۞ੇୱޑᅕᕇౢໆǴԜѦΨૈග ٮҶ໕ᅕ (Kaiser 2006)ǵወНࢲߕуሽॶǵᙖҗЗۭܦаၲډӦߥៈ
(Spieler et al. 2001)ǵբࣁӦޑൺػ܈ံᓭᆶගٮᏢೌࣴزфૈǶ
1.2 Γπങᕛޑᆫങচ
1.2.1 १ނ
ᕛᡏගٮεໆޑ߄य़ᑈٮᝯᜪϷߕғނ (sessile organism) (ӵᚈෘنǵҡ࣑
ྴǵ೬࣑ྴǵੇᆟǵНⶥǵᛯ൙ǵੇᓋᆶऱឿᙝ) բࣁ୷፦аߕϷғߏ (Fitzhardinge and Bailey-Brock 1989; Relini et al. 1994; Svane and Petersen 2001)Ǵӕ ਔΨ֎ЇΑӭੇࢩคૉғނ (ӵλࠠҘෘᜪǵ೬ᡏނ) ᆫ (Sogard 1989;
Relini et al. 2002; Leitão et al. 2007)ǴܫຫΦޑᕛᡏǴᆫޑғނᆶӭኬ܄Ψຫଯ (Sammarco et al. 2004)ǴങᜪޑᙦࡋΨᒿϐቚу (Redman and Szedlmayer 2009)ǶΓ πങᕛޑ߄ғނ (epibiota) ёаբࣁΓπങᕛۓ܄܈ߚۓ܄ങᜪޑ१ނ
ٰྍϐ (Godoy et al. 2002; Sánchez-Jerez et al. 2002; Santos et al. 2011)Ƕ
Moreau et al. (2008) ࡰрǴ߄ғނᗨฅёаගٮങᜪޑ१ނٰྍǴՠၸ౽ ନ߄ғނޑჴᡍύǴങᜪᆫޑຝᆶჹྣಔค౦Ǵёـങᜪ٠όֹӄ٩ᒘᕛ
ᡏ܌ගٮޑ१ނٰྍǴԶᕛᡏҁيҭԖځдচӢ֎ЇങᜪᆫǶ
1.2.2 ܌
ჹܭӭങᜪǴᕛᡏޑҥᡏޜ໔่ᄬૈٮځ৲ǵၧᗉமࠂޑНࢬᆶእ্
(Moreau et al. 2008)ǴᕛᡏҁيڀԖຫӭϾሜǴຫૈගٮጨޑਏᔈǴങᜪޑᙦࡋ ᆶӭኬ܄Ψёૈຫଯ (Hixon and Beets 1989; Brotto et al. 2006)ǶӧѳڶޑੇǴ ΓπങᕛङࢬೀӢࣁНᓸޑᡂϯԋೀࢬೲၨޑୱǴ֎ЇങᜪܭԜ৲
(Nakamura 1985)ǴӕਔᕛᡏኳಔڀԖελϾࢰ܈ࢂ߄ғғނᄬፄᚇჹλങૈග ٮៈǴၧᗉεങޑ१բҔǴׯ๓λങޑӸࢲ (Svane and Petersen 2001; Scharf et al. 2006)Ƕ
ፄᚇࡋଯޑᕛᡏόѝගٮλങ܌ǴӕਔΨёૈගٮ१܄ങᜪၧᙒӧԜ (Hixon and Beets 1989)ǴჹܭλങޑӸࢲԶقǴόӄฅѝԖ҅य़ޑቹៜǶ
1.2.3 ځд
ᕛᡏޑᄬόѝૈගٮߕғނޑभǴΨૈ֎ЇങᜪԿԜᑐணౢռǴࣗ
Կࢌ٤۟ᕛ܄ങᜪޑѴങڙډۓޑག۔ڈᐟǴӵىޑ१ނ܈ࢂԖጨ܄
ޑᄬӢԶӧԜۓϷԋߏ (Bull and Kendall 1994)Ƕ
ჹܭ٤ෞ܄ങᜪԶقǴନΑӢࣁങᕛᆫΑራၗྍԿԜ१ѦǴ ᕛᡏΨૈቹៜځՉࣁǴٯӵӭങᜪૈၸۭ፦ޑࠟޔ่ᄬނ܈ࢂӀጕٰ
ۓӛ܈ۓՏ (Bohnsack 1989)Ƕ٤εࢩ߄ቫ܄ޑങᅿ׳ૈճҔ೭٤Ӧᇮቻբࣁ
ෞБӛୖԵᗺ (Gallaway and Lewbel 1982)Ƕ
1.3 ቹៜΓπങᕛങᜪဂᆫޑӢη
ΓࣴزςࡰрӭቹៜΓπങᕛങᜪဂᆫޑӢηǴԶϩӢηӕኬჹ ᕛᡏޑߕғނ࣬ԋቹៜ (Guerin 2009)ǶΓπങᕛᕛᡏ܌ғߏޑߕғނӭ
ኬ܄ຫଯǵᙟᇂຫଯǴᕛᡏ߄य़ޑ่ᄬፄᚇࡋ൩ຫଯǴ१ނᆶጨ܌ޑගٮǴ ჹങᜪဂᆫԖᡉቹៜ (Hueckel and Buckley 1989; González-Gándara et al. 1999;
Ferreira et al. 2001; Arias-González et al. 2006; Redman and Szedlmayer 2009;
Honório et al. 2010)ǶԜѦǴO’Leary et al. (2001) ᇡࣁǴΓπങᕛޑीх֖ΑǺ Ӧᗺ (location)ǵթᆶ௨ӈ (arrangement)ǵ፦ᆶᄬԋ (composition) ΟӢηǴ Զ೭ΟӢηΞᆶങᜪဂᆫಔԋԖஏϪޑᜢ߯Ƕ
1.3.1 Ӧᗺ
Bohnsack and Sutherland (1985) ᇡࣁΓπങᕛܫޑӦᗺࢂ،ۓങᕛԋ௳ޑ ЬӢǴᕛ܌ӧӦޑᕉნӢηჹܭങᜪဂᆫޑಔԋԖᡉቹៜǶٯӵᕛޑՏ
ᒿጎࡋᡂϯǴНྕߡԖӦᗺ໔ޑৡ౦ (Bortone et al. 1994; Floeter et al. 2004)ǹ၀ Ӧफ़ߘӭჲǵϷᚆݞαޑᇻ߈ǴёૈჹੇНޑᡶࡋౢғ٤༾ޑቹៜǴԶׯᡂ ങᜪဂᆫޑಔԋ (Godoy et al. 2002)ǶങᕛѤڬޑۭ፦ᜪࠠϷੇࢬፂᔐޑம১ǵૈ
ـࡋᆶ؇ᑈނӭჲǴΨჹങᜪᆶۭғނ࣬ԋቹៜ (Baynes and Szmant 1989)Ƕ
ӝങᕛܫޑుࡋऊӧ 20~30 ϦЁ໔ǴᕛᡏܫϼభܰڙݢੁፂᔐԶཞᚯǹ
ܫϼు߾όܰᢀჸǴӀጕऀΚᒿుࡋሀ෧ǴߕғނᆶങᜪဂᆫҭᒿుࡋǴ ӧಔԋΨԖৡ౦ (Ferreira et al. 2001)ǶΓπങᕛᆶϺฅᕛޑຯᚆҭࢂΓπങᕛ
ങᜪಔԋޑᜢᗖǴFast and Pagan (1974) Ϸ Matthews (1985) ֡ჴΓπങᕛޑ ങᜪԖϩٰԾܭϺฅᕛǴӧ Honório et al. (2010) ޑࣴزύΨวΓπങᕛᆶߕ ߈Ϻฅᕛޑങᜪဂᆫಔԋ࣬՟ࡋࡐଯǶ
1.3.2 թᆶ௨ӈ
Γπങᕛޑթᆶ௨ӈЬाх֖Αᕛᡏᡏᑈǵᙟᇂय़ᑈǵᕛᡏଯࡋǵ௨ӈፄ ᚇࡋǶᕛᡏ୴ܫޑᡏᑈ܈߄य़ᑈჹᆫങਏ݀ߚதख़ाǶൂՏᕛᡏ୴᠄ޑᡏᑈຫ εǴ֎Їങᜪޑਏᔈ൩ຫܴᡉ (Ardizzone et al. 1997; Jan et al. 2003)ǹฅԶаӭঁ
ၨλޑᕛ୴ගٮ׳ӭޑ߄य़ᑈǴӧࢌ٤ݩΠޑᆫങਏᔈεܭঁεޑᕛ୴ (Guerin 2009)ǶӧѠчങᕛǴӵ٬Ҕ 2m3НݝᕛǴа 4-10 ঁᕛᡏ୴୴Ǵ ჹቚуۓޣϐғނໆനԖਏǴՠӵஒଽޣӈΕԵቾǴ߾ࡌа 15 ঁᕛᡏࣁ
୴ٰ (Jan et al. 2003)ǶRilov and Benayahu (2000, 2002) ࡰрǴၨଯޑᕛᡏ֎
ЇၨӭޑങᜪǴձࢂ१ੌෞғނޑങᜪǴӧങᜪӭኬ܄ΨԖၨଯޑ߄Ƕҗܭ
ঁᕛᡏჹܭڬᎁڀԖۓጄൎޑቹៜΚǴᕛᡏຯᚆၸ߈ਔǴቹៜޑጄൎख़᠄Ǵ १ނёૈԋࣁज़ڋӢηǴ܈ޣჹۭ፦߄ғ܈ϣғނԋၸଯޑਂ१ᓸΚ (Guerin 2009)ǴSargent et al. (2006) ᇡࣁӧλޑᕛ୴໔ᔈᆢ 30~40 ϦЁޑຯᚆǶ
Ӧޑፄᚇࡋቹៜങဂஏࡋǵғނӭኬ܄Ϸғނໆ (Charbonnel et al. 2002)Ǵ
(2008) ᇡࣁନΑᕛᡏኳಔፄᚇࡋѦǴᔈԵቾޜ໔ፄᚇࡋǴीന٫ޑޑᕛဂթǶ
1.3.3 ፦ᆶᄬԋ
ҔٰࡌങᕛޑёϩࣁϺฅࡌᆶΓπࡌǴх֖ΑԮǵྲྀηǵ
۟ҡǵЕᓐǵНݝǵᒳ៓ǵ༟ጤǵ༟ጤᒳ៓ǵНݝᒳ៓షکǴаϷၗྍӆ ճҔǴаቲకޑ፺जǵً፶ǵᅕಭǵैᝮǵᢕݨѳѠࡌԋᕛᡏǶFitzhardinge and Bailey-Brock (1989) ࡰрӧ࣑ྴӧᒳ៓ᕛғߏၨ፺जᕛؼӳǴНݝᕛߕғނ߾ᆶ Ϻฅᕛၨᜪ՟ǶWalker et al. (2002) КၨҡԪ۟ҡ༧ǵНݝҡషکᕛǵНݝ፺ज షکᕛϐ໔ޑങᅿဂᆫಔԋǴ่݀ΟᅿᕛࠠӧങᅿಔԋؒԖৡ౦ǶMasuda et al.
(2010) ߾วഓ݊ЕങᕛޑങᅿኧᆶғނໆࣣଯܭᗡယЕک༟ጤᆅങᕛǶ
1.4 ങᜪဂᆫᆶ१܄ಔԋ
Bellwood et al. (2002) ᇡࣁǴࣴزεЁࡋғᄊسύޑဂᆫ่ᄬਔǴӚᅿ ᕉნύόӕޑфૈᜪဂǴΑှۓᜪဂӧᕉნύתᄽޑفՅ܈ࢂց٬Ҕᜪ՟ޑၗ
ྍǴКൂપϩғᄊسύނᅿޑಔԋ׳ૈமፓ၀ғᄊسޑރݩᆶՅǶၸᔠຎ १܄фૈဂޑಔԋৡ౦Ǵૈளޕόӕ܌ڀԖޑғᄊཀကᆶၗྍޑճҔ
(Angel and Ojeda 2001; Relini et al. 2002)Ǵ܈ࢂങᜪဂᆫಔԋޑׯᡂჹܭᕉნύ१
܄่ᄬᛙۓ܄ࢂցԖቹៜ (Garrison and Link 2000a)Ƕ
Floeter et al. (2004) ගډങᜪҁيޑ१܄ౣǵ१ނڗளٰྍᆶӦޜ໔ޑ٬
ҔࢂቹៜങᜪණѲᆶӦᒧޑӢηǶᙖҗϩങᜪ१܄фૈဂޑ่ᄬૈᔅ շךॺှങᜪဂᆫԋޑচӢ (Muñoz and Ojeda 1997)Ƕ
1.5 ߈යѠΓπങᕛങᜪဂᆫ࣬ᜢࣴز
ѠԾ҇୯ 62 ԃଆǴഌុӧѠڬᜐੇୱՉΓπങᕛޑǴԿϞςಕᑈ ຬၸ 180,000 ০ǶၸѐՉΓπങᕛਏຑǴӧᅕၗྍҞӭаᅕᕇၗ߄ ҢǴҗܭᒧᅕݤόǵᏹբᅕڀמೌৡ౦ǵਂᕇӦᗺฦᒵᇤৡǴᅕᕇၗ
ྗϯόܰǴЪܰ۹ౣߚᔮ܄ങᅿӧғᄊسύޑख़ा܄Ƕ߈ԃٰǴԖ၏ (2003;
2004) ӧчᕛዬǵࠄᕛዬǵᐱҥᕛǵैᝮᕛǵНݝᕛՉങᜪဂᆫޑፓǴӧ ങᜪޑဂᆫಔԋǴΓπങᕛᆶᐱҥᕛޑၨࣁ࣬߈Ƕ
1.6 ࣴزҞޑ
ѠڬൎੇୱҞӅԖ 88 ೀΓπങᕛ (ᅕᆛઠၗ)ǶᅕԾ 2008 ԃଆଞჹങᕛਏՉද (ഋǴ2008ǹ၏کቅǴ2009Ǵ2010)ǴঋᒵНЎᕉ ნၗǵᕛᡏރݩǵۭߕғނϷങᜪဂᆫǴԿҞࣁЗǴςಕᑈԖ࣬ኧ ໆޑғނ܄ (хࡴങᜪၗྍ) ᆶᕉნၗǶ
ҁࣴزЬाջᔈҔ೭٤ၗǴଞჹаΠҞޑǴޑϩǺ
(1) ၸဂᆫϩǴᔠຎѠڬൎੇୱΓπങᕛങᜪӧဂᆫ่ᄬࢂցૈϩᜪԋ ဂǴӕਔଛӝғނဂᆫࡰǵങᜪᕴ׀ኧᆶғނໆୖኧǴפрόӕෳઠளа ᘜᜪԋဂޑӢηǶ
(2) ϩόӕӦ໔ങᅿಔԋޑৡ౦ǴᙖаפрЬाቹៜϩဂޑങᅿբࣁӚӦ
ޑж߄܄ങᅿǶ
(3) ஒғނӢηᆶᕉნӢηՉ࣬ᜢ܄ϩаϷ௨ׇϩǴפрёૈቹៜങᜪဂᆫ ϩѲޑᕉნӢηǴ٠КၨങᜪဂᆫǵᕉნӢηᆶෳઠϐ໔ޑᜢ߯Ƕ
(4) ၸϩΓπങᕛങᜪޑ१܄ಔԋ่ᄬǴΓπങᕛၗྍޑճҔݩᆶӚ
ੇୱങᜪဂᆫ่ᄬޑቻǶ
ມǵᆶБݤ
2.1 ၗٰྍ
ҁࣴز܌٬ҔᕉნᆶғނၗྍԾܭᅕ܌ޑȨࡀܿϷᆵܿੇୱΓπ ങᕛፓຑπբȩǵȨΓπങᕛᅕਏፓࣴزȩϷȨΓπങᕛᅕਏ
ፓϷёՉ܄ຑȩΟࣴزीฝޑԋ݀ൔਜ (ഋǴ2008ǹ၏کቅǴ2009Ǵ 2010)Ƕ
2.2 ࣴزኬ
ॊΟࣴز܌ளϐၗ఼ᇂ 32 ೀങᕛ (߄ 1)Ǵϩձࣁఈੇࡅǵεݓடǵ ҡࠤǵܿᐞǵεٚǵుᐞǵᐞۭǵԮൎǵ҉Ӽǵཥᙦ (Β)ǵഗǵѦǵқཥǵ ೯ (Β)ǵϖҘǵऽᅽǵࠄᅽǵੇαǵࠄǵ݅ᜐ ()ǵ݅ᜐ (Β)ǵ݅ᜐ (Ο)ǵ
ܽቧ ()ǵܽቧ (Β)ǵܽቧ (Ο)ǵᡶቧǵڻሷǵԮ෫ǵەǵλෝǵਮαᆶᓫ
Γπങᕛ (კ 1)Ƕ
җܭӝಭወբޑਔ໔ڙज़ܭϺϷੇݩǴӢԜӧੇݩᛙۓޑනਟқВ
ՉወНፓǴፓਔ໔வ 2008 ԃډ 2010 ԃ 3 ДԿ 10 ДǶ32 ঁᕛϩձՉ 3 Կ 9 ԛǴӝ 135 ঁෳઠޑങᕛፓǴᕛᡏᜪࠠхࡴНݝᕛǵႝఎᕛǵᒳ៓ᕛǵᅕ ಭᕛϷैᝮᕛ 5 ᅿόӕᜪࠠǶ
2.3 ፓБݤ 2.3.1 ᕉნӢη
2.3.1.1 ߚғނ܄ᕉნӢη
೭٤ൔӅᒵǺঁෳઠӧΠᗕճҔ GPS ෳளΠᗕᗺޑጎࡋၗૻǹΠ ወࡕаుࡋ߄ǵНྕ߄ෳໆᕛᡏ০ပНుǵᕛᡏଯࡋϷНྕǹڰۓೕϐНݝᕛǵ
ႝఎᕛϷᒳ៓ᕛᒵᕛᡏኧໆǴᅕಭᕛϷैᝮᕛᆉᕛᡏߏቨǴளᕛᡏۭय़ᑈǶ
ຑНΠૈـࡋϷෳໆᕛᡏ߄य़ᙟᇂ؇ᑈނࠆࡋǴᒵНΠբਔаϷၸѐН ᡏషᐜࡋၗૻǹۭ፦٩ᕛᡏۭڬᎁಈ৩ελԶۓǴҗܭόӕਔය܌Ҕޑྗό
ǴӢԜӧҁፕЎύਥᏵচԖၗૻǴख़ཥϩࣁ 5 ঁભǺ0Ǵᕛዬǹ1Ǵεࠠ༝ҡǹ 2Ǵ༝ҡǹ3Ǵࣳǹ4ǴݝǶ
2.3.1.2 ғނ܄ᕉნӢη
ۭߕғނճҔ D200 ኧՏൂ࣬ᐒଛٛНෘӧᕛᡏܡྣڗኬǶ٬Ҕ Coral Point Count With Excel extensions (CPCe) ೬ᡏǴीᆉᕴғނᙟᇂаϷӚεᜪۭ
ߕғނޑঁձᙟᇂǴхࡴᝯᜪǵੇᆟǵНⶥǵҡ࣑ྴǵ೬࣑ྴǵੇဗǵ೬ᡏǵ ጺᛵǵᛯ൙ǵऱឿނǵҜނǵੇᓋᆶځд҂ӈΕॊεᜪϐۭғނǶ
2.3.2 ങᜪဂᆫ
ങᜪဂᆫޑፓБԄЬाϩࣁٿεᜪǴନΑճҔӚԄᅕڀǵϯᏢᛰࠔǵࣆᛰ
ஒፓୱങᜪ࣬మନޑਂᕇݤ (capture methods) ϐѦǴҞεӭ٬Ҕჹੇࢩ ᕉნϷғނઇᚯᆶυᘋനեޑᢀჸݤ (observational methods) (Bortone et al. 2000)Ƕ ࡕޣΞаҞຎݤ (underwater visual census) നதᔈҔӧ࣑ྴᕛങᜪဂᆫޑፓ
(Brock 1982)ǶҗܭҁࣴزፓҞࣁڀԖۓଯࡋϐҥᡏ่ᄬᕛᡏǴ٠ߚࢂ༧ ໒ܫޑୱǴࡺ௦Ҕۓਔीኧݤ (interval counts)ǴаᕛᡏࣁύЈǴӧڬᎁᒿᐒْ
ෞ 15 ϩដǴᒵрޑങᅿǵᡏߏϷኧໆ (Williams 1982)Ƕ
2.4 ၗϩ
2.4.1 ၗྗϯ
܌ϩޑᕉნᡂኧх֖Αߚғނ܄ᕉნӢηϷғނ܄ᕉნӢηǴӚঁᡂኧ٬
ҔόӕޑൂՏǴ҂ᗉխൂՏৡ౦ޑυᘋǴஒঁᕉნᡂኧՉྗϯǴаྗϯ ࡕޑᕉნᡂኧՉࡕុϩǶྗϯϦԄࣁǺ
σ X Z X
XǺाྗϯޑॶǹX Ǻ၀ᡂኧޑᆉೌѳ֡ኧǹσǺ၀ᡂኧޑྗৡ
2.4.2 ܄ (residency) ղձ
Γπങᕛങᜪ٩ྣғࢲӧᕛޑਔ໔ᆶჹᕛޑ٩ᒘ܄ǴёϩࣁΟᅿ
܄Ǻۓ܄ (resident)ǵଽ܄ (visitor)ǵၸნ (transient) (Seaman and Sprague 1991)ǶୖԵၸѐЎᒵǴஒҁࣴزύрϐങᅿಉౣϩࣁǺۓ܄ᆶߚۓ܄Ƕ ࣁΑᗉխߚۓ܄ങᅿଽว܄ޑуΕဂᆫǴԋϩޑᚇૻǴҁࣴزଞჹෳ
ઠύۓ܄ങᅿǶ
2.4.3 ങᜪғނໆᆉ
߯ճҔόӕങᅿғߏޑ౦ᘜԄ (allometric equation) W=aLbٰᆉ၀ങᅿ ޑख़ໆǶӚঁങᅿᙯඤޑୖኧୖྣԾ FishBaseǴऩ၀ങᅿલЮᡏߏᡏख़ᙯඤୖኧǴ аᡏࠠ࣬՟ޑӕឦങᅿڗжǶၸᡏߏᆶᕴ׀ኧၗёளӚങᅿޑᕴғނໆǶ
2.4.4 ဂᆫࡰኧ
2.4.4.1 ނᅿᙦࡋࡰ (species richness index) D = (S -1/log N)
SǺނᅿኧǹNǺᕴঁᡏኧǶD ॶຫଯ߄Ң၀ෳઠނᅿᅿᜪຫᙦǶ
2.4.4.2 ӭኬ܄ࡰ (diversity index)
ճҔ Shannon diversity index (H’) բࣁෳઠғނӭኬ܄ࡰǴж߄Ӛෳઠঁᡏ ᆶނᅿޑ֡ϬำࡋǶH’ॶຫଯǴ߄Ң၀ෳઠဂᆫނᅿຫӭ܈ᅿ໔ঁᡏϩଛၨ֡
ϬǶ
¦
S
i Pi Pi
H'
1
log
SǺԛፓ܌ᒵډޑങᅿኧǶ
PiǺԛፓਔǴಃ i ᅿങᅿϐঁᡏኧᆶᕴങᅿঁᡏኧКॶǶ
2.4.4.3 ֡Ϭࡋࡰ(evenness index)
Pielou’s evenness (J’) ࢂҗ Shannon diversity index ़՜ԶٰǶճҔෳઠύᅿ໔
ঁᡏϩଛޑ֡Ϭำࡋᆶӭኬ܄ࡰኧനεॶ (Hmax) КၨǴঁނᅿޑኧໆठਔǴ
֡Ϭࡋࣁ 1ǴࣁғނӧෳઠύኧໆϩѲޑࡰǶ J’ = H’/Hmax=H’/log S
H’ǺShannon diversity index
2.4.5 Ӧੇୱᆶᕛࠠϩ
ճҔ Kruskal-Wallis ൂӢηભᡂ౦ኧϩ (Kruskal-Wallis ony-way analysis of variance by rank, Kruskal-Wallis Test) ᔠෳѤঁӦޑӚᅿဂᆫࡰࢂցԖৡ౦Ƕ ऩੇୱ໔Ԗৡ౦Ǵа Mann-Whitney Test ᔠෳٿੇୱ໔ဂᆫࡰޑৡ౦Ƕ ჹܭӚੇୱϐϣǴဂᆫࡰࢂӢόӕᕛࠠԶ౦Ǵӕኬа Kruskal-Wallis Test Ϸ Mann-Whitney TestՉᔠۓǶ
ԜѦǴӧᕴ׀ኧᆶғނໆ೭ٿᡂኧБय़Ǵҭ٬Ҕค҆ኧᔠۓБݤǴϩձᔠ
ෳόӕӦϷόӕᅿᕛࠠǴჹങᜪᕴ׀ኧᆶғނໆࢂցԖቹៜǶ
ჹܭӚੇୱύόӕᕛࠠჹܭဂᆫ่ᄬޑቹៜǴ߾ճҔ࣬՟ࡋϩ (analysis of similarities, ANOSIM) ٰᔠۓǴҗભ࣬՟ࡋંତٰीᆉ R ॶǶR ॶૈ߄Ң όӕᕛࠠ໔ဂᆫ่ᄬޑৡ౦ำࡋǴ R ࣁ 1 ਔǴ߄Ңӕᕛࠠޑ࣬՟ࡋεܭᕛࠠ໔ ޑ࣬՟ࡋǹ R ॶ߈Я 0 ਔǴ߄Ңᕛࠠϣکᕛࠠ໔ޑ࣬՟ࡋؒԖৡ౦ǶԶقǴ
R>0.75 ਔǴ߄Ңٿဂᆫ่ᄬڀԖཱུεৡ౦ǹԶ R<0.25 ਔǴ߾߄Ңဂᆫ่ᄬ
൳ЯؒԖৡ౦ (Clarke 1993)Ƕ
4 / ) 1 (
) (
n n
r R rB W
rB Ǻᕛࠠ໔ભ࣬՟ࡋϐѳ֡ǹrW Ǻᕛࠠϣભ࣬՟ࡋϐѳ֡ǹnǺᕴෳઠኧ
2.4.6 ဂᆫ่ᄬϩ
ဂᆫ่ᄬ߯а Primer v6 (Clarke and Gorley 2006) း೬ᡏՉϩǶӧ 135
ঁෳઠޑങᕛፓύǴԌନߚۓ܄ޑങᅿǴஒങᜪဂᆫၗၸ log(x+1) ᙯ ඤǴीᆉ୷ܭ Bray-Curtis ຯᚆޑ࣬՟ࡋંତǶа໘ቫԄဂϩݤ (hierarchical cluster analysis) ᆶߚीໆӭӛࡋໆЁݤ (non-metric multi-dimensional scaling, MDS) КၨόӕӦങᅿಔԋޑ࣬՟ࡋǶᕉნၗ߾ՉЬԋϩϩ (principal components analysis, PCA)ǴפрԋόӕӦᕉნৡ౦ޑЬाӢηǶ
ԜѦǴၸ BIO-ENV (biota and/or environment matching) ஒဂᆫၗᆶᕉნᡂ ኧբೱ่ǶόӕᕉნӢηಔӝ୷ܭኻԄຯᚆ (Euclidean distance) ԋᕉნӢηં
ତǴނᅿဂᆫಔԋԋ Bray-Curtis ࣬՟܄ંତǴीᆉٿϐ໔ Spearman ભ࣬ᜢ
߯ኧ (Spearman’s rank correlation coefficient)Ǵ࣬ᜢ܄നଯޑᕉნӢηಔӝ߾നૈ
ှញങᅿဂᆫಔԋޑৡ౦ (Clarke 1993)Ƕ
2.4.7 ௨ׇϩ (ordination)
а௨ׇϩғނဂᆫ܈ኬӧᕉნఊࡋޑϩѲǴᙖаפрቹៜғ ނဂᆫᡂ౦ޑЬाᕉნӢηǶҁࣴزϩձ٬Ҕڂࠠჹᔈϩ (canonical
correspondence analysis, CCA) ϷϧᎩϩ (redundancy analysis, RDA) ٿᅿϩ
БݤǶനதҔٰϸᔈނᅿᆶᕉნᜢ߯ޑኳࠠԖٿᅿǴᅿࣁጕ܄ኳࠠ (linear model)Ǵ ќᅿࣁൂঢ়ኳࠠ (unimodal model)Ƕނᅿӧᕉნఊࡋևጕ܄ϩѲਔǴ٬Ҕ ϧᎩϩǹऩނᅿӧᕉნఊࡋԖനॶ (optimun)Ǵևដޑൂঢ়ϩѲਔǴ٬
ҔڂࠠჹᔈϩǶኳࠠޑᒧڗ،ܭफ़ᖿჹᔈϩ (detrended correspondence
analysis, DCA) ఊࡋືߏࡋޑϩǶಃঁఊࡋືεܭѤঁྗৡਔǴ٬Ҕڂࠠ
ჹᔈϩǹऩλܭΟঁྗৡਔǴ߾٬ҔϧᎩϩ (ter Braak and Šmilaue 2002)Ƕ നࡕճҔᆾӦьᛥඤᔠᡍ (Monte Carlo permutation test) ᔠෳ࣬ᜢޑᕉნӢη
ࢂցၲᡉНྗ (Lepš and Šmilauer 2003)Ƕ
җܭ܌ᔈҔޑၗύങᅿӭǴԶځύёૈԖ٤ങᅿӧϩѲёૈᆶҁࣴ
ز܌ԵቾϐᕉნӢηؒԖᡉ࣬ᜢǴΞ܈ޣԖၠӭϩѲޑǴ܈ങᅿӧᕛ
ύޑрࣁଽว٣ҹǴ܈ങᅿϩѲጄൎᇻλܭҁࣴزύ܌ჄۓޑӦϩǴӢ Ԝᙖҗ Primer ύޑ SIMPER (similarity percentages) ϩǴीᆉрӦϣǴჹܭ ങᅿಔԋ࣬՟ࡋଅଯޑങᅿǹ٠Ъीᆉ၀ӦᆶځдӦങᅿಔԋ࣬౦ࡋଅ
ଯޑങᅿǴᒧӕਔჹٿޣଯࡋଅޑങᅿനࣁ၀ޑж߄ങᅿǴၸ௨ׇݤ
Զפр೭٤ങᅿϩѲӧۓୱޑำࡋǶᙖҗჹ೭٤ж߄܄ങᅿϩǴૈ׳
మධޑᕕှӚӦ܄ᕉნӢηޑቹៜำࡋǶ
2.4.8 १܄ಔԋϩ
ஒঁෳઠ܌ፓډޑങᅿǴୖԵၸѐЎᒵᆶ FishBase ങᅿ१ނ࣬Ǵ ϩࣁ 8 ᅿ१܄ᜪဂǺᝯ१܄ (herbivores)ǵੌෞނ१܄ (planktivores)ǵۭคૉ
ނ१܄ (benthic invertebrate feeders)ǵ१ങ१܄ (piscivores)ǵ࣑ྴᙝ१܄
(corallivores)ǵᚇ१܄ (omnivores)ǵԺ१܄ (carnivores)ǵమዅ१܄ (cleaners) (Jennings et al. 1995; Jennings and Polunin 1996; Ferreira et al. 2001; Khalaf and Kochzius 2002; Ferreira et al. 2004; Ferreira and Gonçalves 2006; Cole et al. 2008;
Honório et al. 2010)Ƕ࣑ྴᙝ१܄хࡴ܄ (obligate) ࣑ྴᙝ१܄ᆶҭ१ᝯᜪᆶ
ۭคૉނޑঋ܄ (facultative) ࣑ྴᙝ१܄Ƕᚇ१܄ж߄ӕਔӞᝯᜪϷੌෞ
ނ܈ۭคૉނǶԺ१܄ж߄ӕਔӞۭคૉނϷങᜪ܈ੌෞނǶమ ዅ१܄аځдങᡏѦғނ܈ᡏ߄ϩݜޑᗹనࣁ१Ƕځύঋ܄࣑ྴᙝ१܄ǵᚇ१
܄ᆶԺ१܄ങᅿൺ٩ྣ१ނٰྍǴஒғނໆѳ֡યΕᝯ१܄ǵੌෞނ१܄ǵۭ
คૉғނ१܄ǵ१ങ१܄ǵ࣑ྴᙝ१܄ύǴаीόӕӦങᅿჹܭόӕၗ
ྍޑሡำࡋǶ
аങᅿᕴ׀ኧϷғނໆၗीᆉӚঁෳઠ१܄่ᄬಔԋޑኧໆԭϩКᆶख़ໆ ԭϩКǴ٠уа࣬ϕКၨǶ
ୖǵ่݀
3.1 ങᜪဂᆫϩ
܌Ԗෳઠ٩ྣങᜪޑဂᆫ่ᄬޑಔԋёаϩࣁѤঁܴᡉޑᜪဂ (კ 2)Ǵஒ 4
ঁᜪဂ٩ྣӦϩѲϩࣁǺч (62 ઠ)ǵՋࠄ (25 ઠ)ǵܿࠄ (30 ઠ) Ϸᚆ (18 ઠ)Ƕځύܽቧ (Ο) ෳઠჄΕܿࠄǴεݓடෳઠᆶԮൎٿෳઠჄΕՋ ࠄǴࣁୃᚆځচٰӦϩޑϿኧෳઠǶѤঁဂύǴчᆶՋࠄങᜪဂᆫಔ ԋၨᜪ՟Ǵܿࠄ߾ᆶᚆၨ࣬՟ǶMDS ϩ่݀ (კ 3Ǵstress=0.16) ύǴчǵ ՋࠄᆶܿࠄΟޑಔԋ࣬՟ࡋӧѳय़ޜ໔ևΟفϩѲǴԶᚆ߾ᆶܿࠄၨᜪ
՟Ƕၸ SIMPER ϩӚঁဂങᜪဂᆫಔԋޑѳ֡࣬౦ࡋ(average dissimilarity) ёှញෳઠӧ MDS კޑϩѲ (߄ 2)Ƕ
3.2 Ӧᆶᕛࠠϩ
3.2.1 ങᜪဂᆫ่ᄬ
ӧങᜪဂᆫ่ᄬБय़ǴӃޑဂϩᡉҢങᜪဂᆫԖӦ܄ޑৡ౦Ƕၸ one-way ANOSIMଞჹ 4 ঁӦϩձǴࢂցᕛࠠޑৡ౦ҭቹៜങᜪဂᆫޑ ಔԋǶ
ӧчᕛύӅԖНݝᕛ (рܭ 18 ෳઠ)ǵႝఎᕛ (15 ෳઠ)ǵᒳ៓ᕛ (23
ෳઠ)ǵᅕಭᕛ (3 ෳઠ) Ϸैᝮᕛ (3 ෳઠ) ϖᅿᕛࠠǴങᜪဂᆫಔԋӧᕛࠠ໔൳ ЯؒԖৡ౦ (ANOSIM, global R=0.104)Ƕ
ՋࠄᕛύӅԖНݝᕛ (6 ෳઠ)ǵႝఎᕛ (2 ෳઠ)ǵᒳ៓ᕛ (8 ෳઠ)ǵᅕಭᕛ (9ෳઠ) ѤᅿᕛࠠǴങᜪဂᆫಔԋӧᕛࠠ໔ҭΜϩᜪ՟ (ANOSIM, global
R=0.224)Ƕ
ܿࠄᕛύӅԖНݝᕛ (7 ෳઠ)ǵႝఎᕛ (12 ෳઠ)ǵᒳ៓ᕛ (7 ෳઠ)ǵैᝮ ᕛ (4 ෳઠ) ѤᅿᕛࠠǴങᜪဂᆫಔԋӧᕛࠠ໔Ԗৡ౦Ӹӧ (ANOSIM, global
R=0.29)ǴࣁΑᕕှব٤ᕛࠠԋৡ౦ǴӢԜՉᕛࠠϐ໔ޑଛჹϩ (pairwise tests)Ǵ่݀วᒳ៓ᕛᆶैᝮᕛޑങᜪဂᆫಔԋԖᡉৡ౦ (R=0.926) (߄ 3)Ƕ
ᚆᕛӅԖႝఎᕛ (6 ෳઠ)ǵᒳ៓ᕛ (5 ෳઠ)ǵैᝮᕛ (7 ෳઠ) ΟᅿᕛࠠǴ ങᜪဂᆫಔԋӧᕛࠠ໔ҭԖৡ౦ (ANOSIM, global R=0.343)ǴଛჹϩύǴႝఎᕛ ᆶᒳ៓ᕛ໔ӧങᅿಔԋԖᡉৡ౦ (R=0.824) (߄ 4)ǶчᆶՋࠄޑෳઠǴങ ᜪဂᆫಔԋӧѤᅿόӕᕛࠠ໔ؒԖܴᡉৡ౦Ǵܿࠄᆶᚆޑෳઠϩᕛࠠ໔ Ԗৡ౦Ƕ
3.2.2 ғނဂᆫࡰޑКၨ
аނᅿᙦࡋࡰǵӭኬ܄ࡰᆶ֡ϬࡋࡰբࣁғނဂᆫࡰǴΟᡂኧ ϩձՉ Kruskal-Wallis Test ᔠᡍੇୱ໔ဂᆫࡰࢂցԖৡ౦Ǵ่݀ᡉҢނᅿᙦ
ࡋࡰ (Kruskal-Wallis test, ͞2=91.074, p<0.001)ǵӭኬ܄ࡰ (Kruskal-Wallis test,
͞2=57.215, p<0.001) Ϸ֡Ϭࡋࡰ (Kruskal-Wallis test, ͞2=28.013, p<0.001) ӧ ѤঁӦࣣԖᡉৡ౦ (߄ 5Ǵკ 4)Ǵа Mann-Whitney Test КၨٿٿӦ໔ғނ ဂᆫࡰޑৡ౦ǴӧނᅿᙦࡋࡰБय़Ǻᚆ > ܿࠄ > ч > Ջࠄǹӭ ኬ܄ࡰБय़Ǻᚆ > ܿࠄ > ч = Ջࠄǹ֡ϬࡋࡰБय़Ǻᚆ > ܿࠄ = Ջ ࠄ > ч (߄ 6)Ƕ
ѤঁӦϩձӆа Kruskal-Wallis Test ϩӕӦϣόӕᕛࠠࢂցჹғނဂᆫ
ࡰԋቹៜǴ่݀ᡉҢѤঁӦϣόӕᕛࠠޑΟᅿғނဂᆫࡰࣣคᡉৡ౦ (߄ 7)Ƕ
3.2.3 ങᜪᕴ׀ኧ܈ғނໆޑৡ౦܄
ၸങᅿᡏߏᆶᕴ׀ኧၗीᆉӚঁങᅿғނໆǴӆஒঁෳઠрޑങᅿ уᕴளډӚঁෳઠޑᕴғނໆǶճҔ Kruskal-Wallis Test ᔠᡍѤঁӦങᜪᕴ׀ኧ ᆶғނໆࢂցԖৡ౦Ǵ่݀ᡉҢᕴ׀ኧ (Kruskal-Wallis test, ͞2=23.625, p<0.001)
܈ғނໆ (Kruskal-Wallis test, ͞2=18.72, p<0.001) ӧѤੇୱࣣԖᡉৡ౦ (߄ 8Ǵკ 5)Ƕа Mann-Whitney Test КၨٿӦ໔ᕴ׀ኧᆶғނໆޑৡ౦Ǵӧ ᕴ׀ኧБय़Ǻч = ܿࠄ > Ջࠄ = ᚆǹғނໆБय़Ǻܿࠄ > ᚆ = ч> Ջ ࠄ (߄ 9)Ƕ
Ѥੇୱϩձӆа Kruskal-Wallis Test ϩӕੇϣόӕᕛࠠࢂցჹᕴ׀ኧ܈
ғނໆԋቹៜǴ่݀ᡉҢѤঁӦύޑᕛࠠёૈჹᕴ׀ኧ܈ғނໆౢғቹៜ (߄ 10)Ƕчᕛғނໆӧᕛࠠ໔Ԗᡉৡ౦ (Kruskal-Wallis test, ͞2=12.882, p=0.012) (კ 6Ǵ߄ 11)Ǵၸ Mann-Whitney Test Кၨٿٿόӕᕛࠠৡ౦ࡕǴैᝮ ᕛᆶᒳ៓ᕛғނໆᡉଯܭНݝᕛᆶᅕಭᕛǴᕴ׀ኧБय़߾คᡉৡ౦ǹՋࠄᕛ
ғނໆӧᕛࠠ໔ҭԖᡉৡ౦ (Kruskal-Wallis test, ͞2=8.911, p=0.031) (კ 6Ǵ ߄ 11)ǴMann-Whitney Test ่݀ᡉҢᅕಭᕛғނໆᡉଯܭНݝᕛǴԶᕴ׀ኧคᡉ
ৡ౦ǹܿࠄᕛᕛࠠӕኬӧғނໆԋᡉৡ౦ (Kruskal-Wallis test, ͞
2=19.86, p<0.001) (კ 6Ǵ߄ 11)ǴMann-Whitney Test ่݀ᡉҢόӕᕛࠠғނໆελ ޑৡ౦ࣁǺैᝮᕛ > ႝఎᕛ = ᒳ៓ᕛ > НݝᕛǴᕴ׀ኧБय़ҭคᡉৡ౦ǹ ᚆᕛᕴ׀ኧӧᕛࠠ໔Ԗᡉৡ౦ (Kruskal-Wallis test, ͞2=8.911, p=0.031) (კ 6Ǵ߄ 11)ǴMann-Whitney Test ่݀ᡉҢόӕᕛࠠᕴ׀ኧӭჲޑৡ౦ࣁǺႝఎ ᕛ > ᒳ៓ᕛ = ैᝮᕛǶ
3.3 ᕉნӢηЬԋϩϩ
ࣁΑஒӚങᕛၨόቹៜങᜪဂᆫޑۭғނᙟᇂ௨ନǴԶՉҁϩǶ २Ӄа 12 ᅿۭғނᙟᇂՉЬԋϩϩ (PCA)Ǵϩ܌ளϐಃືЬाӢη ࣁᝯᜪǴಃΒືࣁੇᆟᆶ೬࣑ྴǴٿঁື܌ಕᑈૈှញᡂ౦ޑໆࣁ 65.4% (კ 7)Ƕ ਥᏵԜ่݀Ǵஒځύቻӛໆ (eigenvectors) ၨλޑӢηǴхࡴੇဗǵ೬ᡏǵҘ
ෘᜪǵҜނϷऱឿނуа௨ନǴќаቻӛໆၨଯޑΎᅿۭғނӢηǴ уНྕǵᕴᙟᇂǵۭ፦ᜪࠠǵ؇ᑈނࠆࡋϷૈـࡋՉЬԋϩϩǶ่݀
ᡉҢǴӧങᜪဂᆫޑϩύǴܿࠄǵᚆങᕛޑᝯᜪᙟᇂǵᕴғނᙟᇂϷ
ૈـࡋၨଯǹՋࠄങᕛ߾ۭ፦ၨಒǵᕛᡏ؇ᑈނၨࠆ (კ 8)Ƕ
3.4 ᕉნӢηᆶങᅿಔԋᜢ߯
а BIO-ENV БݤਥᏵӭᕉნӢηಔӝीᆉᆶങᜪဂᆫಔԋޑ࣬ᜢ܄Ǵ൨פ
ԋങᜪဂᆫಔԋৡ౦ޑЬाᕉნӢηǴ่݀ᡉҢۭ፦ᜪࠠǵૈـࡋᆶጎࡋࢂ
ԋৡ౦ޑЬाᕉნӢη (͙w=0.647) (߄ 12)Ƕ
3.5௨ׇϩ
२ӃஒങᅿޑဂᆫၗՉफ़ᖿჹᔈϩ (DCA)Ǵᒧаڂࠠჹᔈϩ
(CCA) ࣁ௨ׇޑኳࠠǶෳઠᆶᕉნᡂໆӧಃఊࡋືکಃΒఊࡋືޑϩѲа ᚈׇკ (bioplot) ߄Ң (კ 9)ǶှਔǴෳઠᆶෳઠ܈ނᅿᆶނᅿ໔ޑຯᚆࣁьБ ຯᚆ (Chi-square distance)Ǵຫௗ߈߄Ңෳઠӧނᅿಔԋޑৡ౦܄ຫλ܈ࢂނᅿޑ ϩѲৡ౦ၨλǶᕉნᡂኧጂᓐ໔ޑ֨فё߄ҢᕉნӢη໔ޑ࣬ᜢ܄Ǵऩ֨فև 90 ࡋ߾ࣁό࣬ᜢǹෳઠᆶᕉნᡂໆϐ໔ޑᜢ߯߾ёճҔෳઠჹᕉნӢηጂᓐБӛ
ቹ߄ҢǶკύᡉҢǴӃϐങᜪဂϩϩԋޑѤεᜪဂϣޑӚങᕛҭᆙஏ ϩѲԋဂǴځύᆶಃ௨ׇື࣬ᜢ܄ၨεޑᕉნӢηϩձࣁૈـࡋ (࣬ᜢ߯ኧǺ 0.849)ǵᝯᜪ (0.6523)ǵᕴғނᙟᇂ (0.427)ǵጎࡋ (-0.6597)ǵۭ፦ᜪࠠ (-0.6488) ᆶ؇ᑈނࠆࡋ (-0.4889)Ǵ೭٤ӢηӕਔૈှញᚆǵܿࠄෳઠޑϩຝǶԜ ѦǴᆶಃΒ௨ׇື࣬ᜢ܄ၨεޑᕉნӢηЬाࣁጎࡋ (-0.5525)Ǵځ٠Ъёૈࢂ
ԋчෳઠᆶՋࠄෳઠϩᚆޑख़ाӢηǶ
а SIMPER פрӚޑж߄ങᅿ (߄ 12)ǴϩձࣁчǺᐪ׀Ӏភഒ᜶ (Chromis fumea)ǵΟጕᚊങ (Parapristipoma trilineatum)ǵъጕϺޞ᜶ (Apogon semilineatus)ǵ ጂϺޞ᜶ (Rhabdamia gracilis) ϷϤඬΒᏁⰦ (Diodon holocanthus)Ƕഒ᜶ᆶϺޞ᜶
ࣣឦܭ۟ᕛ܄ဂۚങᜪǴ१ੌෞғނ܈λࠠคૉނǹϤඬΒᏁⰦୃӳܭݝ
೬ۭ፦ਂ१ۭคૉނǹဂෞ܄ޑΟጕᚊങ౽ૈΚ٫ǴෞܭӚঁᕛ
ڬᎁޑ፦ۭ፦१ǶՋࠄǺᙔཥഒ᜶ (Neopomacentrus cyanomos)ǵआᔕ
ᢙ (Pseudanthias rubrizonatus) ϷୁϺޞ᜶ (Apogon pleuron)ǶୁϺޞ᜶ᆶआ
ᔕᢙࣣୃӳݝۭ፦ޑੇୱǹᙔཥഒ᜶߾தـܭ۞ᜐ܈ѦੇޑᕛǶܿࠄǺ Ѥᚊങ (Pomadasys quadrilineatus)ǵߎᔕᢙ (Pseudanthias squamipinnis)ǵ
যങ (Labroides dimidiatus)ǵқ֍ᚈҥᄡ᜶ (Heniochus acuminatus) Ϸᒯ׀᜶
(Prionurus scalprum)ǶѤᚊങឦܭቶݱϩѲޑങᅿǴᕛ۟ᆶӦࣣёـǹߎᔕ
ᢙǵқ֍ᚈҥᄡ᜶ᆶযങࣣ৲ങ࣑ྴᕛੇୱǹᒯ׀᜶߾ෞܭӚঁᕛ໔Ƕ ᚆǺፃඬڈ׀᜶ (Acanthurus nigrofuscus)ǵլМጷጸങ (Chaetodon kleinii)ǵ Οඬ༝ഒ᜶ (Dascyllus trimaculatus)ǵߎᔕᠣ᜶ (Mulloidichthys vanicolensis) Ϸ ف៑ങ (Zanclus cornutus)Ƕፃඬڈ׀᜶ឦܭభНୱങᅿǴЬा৲ܭᕛҡޑۭǹ լМጷጸങᆶΟඬ༝ഒ᜶Ьा৲ܭ࣑ྴᕛੇୱǹف៑ങ߾தـܭమᅒޑ࣑ྴᕛ
܈۟ᕛǹߎᔕᠣ᜶ୃӳӧᕛࣳషӝೀ܈ᕛѦൎࣳݝӦ१Ƕ
ନΑᔠຎ೭٤ങᅿޑ৲ᕉნѦǴࣁΑᔠຎ೭ 18 ങᅿޑж߄܄Ǵа೭٤ങᅿ ख़ཥՉ௨ׇϩǹၸ DCA ϩࡕᒧൂঢ়ኳࠠޑ CCAǶϩ่݀аΟׇკ (triplotǴკ 10) ߄ҢނᅿǵෳઠᆶᕉნӢη໔ޑ࣬ᜢ܄ (ނᅿᆶෳઠຫௗ߈߄Ң၀ ނᅿӧ೭٤ෳઠύޑ࣬ჹᙦࡋၨଯ)ǶӧΟׇკύǴԜ 18 ᅿങᅿዴჴϩձᆶ܌ឦෳ
ઠޑຯᚆၨࣁௗ߈ǴӢԜёຎࣁ၀Ӧж߄܄ങᅿǶ
а DCA ϩӚӦж߄܄ങᅿ܌ᄬԋϐဂᆫޑఊࡋߏࡋǴᡉҢӚဂᆫޑ ఊࡋືࣣλܭ 3 ঁྗৡǴӢԜ٬Ҕ୷ܭጕ܄ኳࠠޑϧᎩϩ (RDA) ᝩុуаϩ
Ƕ
ӧᚈׇკύǴނᅿᆶᕉნӢηጂᓐ໔ޑ֨فж߄۶Ԝޑ࣬ᜢ܄ǶӧчǴᆶ
ಃ௨ׇື࣬ᜢ܄ၨεޑᕉნӢηࣁጎࡋ (-0.7235) Ϸᛯ൙ᙟᇂ (-0.5038)ǹಃ
Β௨ׇືࣁ؇ᑈނࠆࡋ (0.4641) (კ 11)Ƕॊ่݀аᆾӦьᛥᔠۓуаᡍ
ǴᡉҢቹៜчᕛങᅿϩѲޑЬाᕉნӢηࣁጎࡋǵࡋǵҡ࣑ྴᙟᇂǵ
؇ᑈނࠆࡋϷᛯ൙ᙟᇂ (߄ 14)ǶӧՋࠄБय़Ǵᆶಃ௨ׇື࣬ᜢ܄ၨεޑᕉ ნӢηࣁۭ፦ᜪࠠ (0.4347) ᆶࡋ (-0.4621) (კ 12)ǶᆾӦьᛥᔠۓǴቹៜՋ ࠄᕛങᅿϩѲޑЬाᕉნӢηࣁࡋǵۭ፦ᜪࠠǵጎࡋǵૈـࡋϷుࡋ (߄ 14)Ƕ
ܿࠄύǴᆶಃ௨ׇື࣬ᜢ܄ၨεޑᕉნӢηࣁጎࡋ (-0.3937)ǴಃΒ௨ׇືࣁ
ੇᆟᙟᇂ (0.3544) (კ 13)ǶᆾӦьᛥᔠۓǴቹៜܿࠄᕛങᅿϩѲޑЬा
ᕉნӢηࣁጎࡋǵࡋǵᕛᡏଯࡋǵНⶥᙟᇂǵੇᆟᙟᇂǵᕴғނᙟᇂϷ
ۭ፦ᜪࠠ (߄ 14)ǶӧᚆύǴᆶಃ௨ׇື࣬ᜢ܄ၨεޑᕉნӢη٩ׇࣁૈـ ࡋ (0.829)ǵᝯᜪᙟᇂ (0.5908)ǵጎࡋ (-0.5333) Ϸۭ፦ᜪࠠ (-0.5033) (კ 14)Ƕ
ᆾӦьᛥᔠۓǴቹៜᚆᕛങᅿϩѲޑЬाᕉნӢηࣁૈـࡋǵጎࡋǵᕴ ғނᙟᇂǵۭ፦ᜪࠠǵࡋǵ೬࣑ྴϷҡ࣑ྴᙟᇂ (߄ 14)Ƕ
3.6 १܄ಔԋϩ
чᕛӧ१܄่ᄬಔԋޑኧໆԭϩКǴКٯനଯޣࣁੌෞނ१܄
(57.1%)Ǵځԛࣁۭคૉނ१܄ (39.15%)Ƕၸख़ໆԭϩК߾ёวੌෞ
ނ१܄ϐख़ໆόଯ (11.24%)Ǵۭคૉނ१܄ӧчࣁനЬाޑᜪဂ (69.08%)ǴӵΟጕᚊങ (Parapristipoma trilineatum) ᆶచҡ᜶ (Oplegnathus
fasciatus)ǴԶҡඬങ (Epinephelus lanceolatus)ǵᅦЃҡඬങ (E. malabaricus)ǵ ሌદಂ᜶ (Lutjanus argentimaculatus) Ժ१܄ങᅿኧໆᗨϿǴՠځғނໆჹ१
ۭคૉނϷ१ങ१܄ᜪဂޑғނໆԖϩଅ (߄ 15)Ƕ
Ջࠄᕛӧ१܄่ᄬಔԋޑኧໆԭϩКǴКٯനଯޣࣁۭคૉނ१
܄ (41.57%)ǴǴځԛࣁੌෞނ१܄ (31.66%) ϷԺ१܄ (20.75%)Ƕੌෞނ१
܄ჹᕴғނໆଅόଯ (7.29%)ǴԺ१܄ޑሌદಂ᜶ (L. argentimaculatus)ǵᅦ
Ѓҡඬങ (E. malabaricus)ǵΐڈ〝ឦ҂᠘ۓᅿ (Cephalopholis sp.) ᆶ१ۭค
ૉނޑൂඬಂ᜶ (L. monostigma) ᆶ೬য (Plectorhinchus cinctus) ޑғނໆ ࣁԜЬा१܄ᄬԋ (߄ 15)Ƕ
ܿࠄᕛӧኧໆ՞ᓬ༈ޑࣁੌෞނ१܄ (34.38%)ǵۭคૉނ१܄
(34.09%) Ϸ࣑ྴᙝ१܄ (17.46%)ǴԶԜమዅ१܄܌՞ޑኧໆКӧѤύനଯ (0.96%)Ƕӧख़ໆԭϩКǴۭคૉނ१܄ҁيғނໆόեѦǴᚇ१܄ޑങ ᜪӵᒯ׀᜶ (Prionurus scalprum)ǵ᠄ݢᇂڈങ (Pomacanthus semicirculatus) ჹ ܭᝯ१܄ (20.24%) Ϸۭคૉނ१܄ (58.6%) ޑғނໆԖόϿଅ (߄ 15)Ƕ
ᚆᕛӧങᅿ१܄่ᄬಔԋޑኧໆԭϩКܴᡉύӧੌෞނ१܄
(71.77%)Ǵځд१܄ᜪձޑങᅿӧᚆᡉள࣬ჹีϿǶவख़ໆԭϩКٰ࣮Ǵᝯ१܄
ޑКख़ౣեܭܿࠄᕛ (10.81%)Ǵ࣑ྴᙝ१܄߾کܿࠄᕛৡόӭ (1.38%)Ǵੌ
ෞނ१܄ (44.42%) کۭคૉނ१܄ (39.04%) ܌՞ޑख़ໆЬाҗ၀
Ժ१܄ങᜪӵඬߎ㲸 (Cirrhitichthys aprinus)ǵᡖيᇘૅ㋗ (Gymnothorax eurostus)ǵ ߎ㲸 (C. aureus) ܌ଅǶ
စǵፕ
4.1 ΓπങᕛܫޑՏᆶങᜪဂᆫ่ᄬ
ᆕӝၸѐ٤ଞჹѠڬൎੇୱୱ܄ޑങᜪဂᆫࣴز܈ғᄊፓൔύǴ Ѡޑ࣑ྴᕛങᜪޑဂᆫಔԋЬाڙډዊᆶࠄੇ߄ቫНٿεНიޑቹៜǴځ ύǴࠄǵܿǵλౚǵើᔁϷᆘڙډዊ܌ቹៜǴӦޑങռ܈в
ങёૈᙖҗྕཪᆶჲᔼᎦᡶޑዊΕࠄੇୱۓǹчᆶዋ෫ੇୱ߾ڙډ ࠄੇ߄ቫН܌ቹៜǴоۑൣհޑύ୯ݮ۞ࢬࠄΠૈ٬Нྕեܭ 20кǴԋങᜪ࣬
ӧࠄчٿεӦᡉޑৡ౦ (Chen et al. 1992; Shao et al. 1993ǹᔎǴ2006)ǶਥᏵ
ဂϩᆶ MDS ޑ่݀ (კ 2Ǵკ 3)ǴѠڬൎੇୱΓπങᕛങᜪဂᆫ٩ങᅿ ಔԋ࣬՟ࡋϩࣁчϷՋࠄǵܿࠄϷᚆٿεᜪဂǴᆶ Shao et al. (1997) ϩѠ
ڬᎁΖೀϺฅᕛങᜪဂᆫಔԋޑဂϩ่݀࣬ᜪ՟ǶନΑങᜪဂᆫಔԋѦǴ
࣑ྴނᅿᙦࡋᆶᕛբҔமࡋҭᒿᕉნచҹޑৡ౦ևчᆶܿࠄǵᚆٿ εϩဂ (ᔎǴ2006)ǶܿࠄǵᚆੇୱғߏೲၨזޑືϾ࣑ྴᆶജف࣑ྴૈԋ
ၨፄᚇޑҥᡏޜ໔Ǵӧ࣑ྴᕛങᜪޑӦϩѲڀԖ࣬ޑቹៜ (Shao et al.
1997)Ƕ
ճҔނᅿᙦࡋ (D)ǵӭኬ܄ (H’) Ϸ֡Ϭࡋ (J’) ΟᅿဂᆫࡰٰှញѤঁ
ӦങᜪဂᆫǴ่݀ࡰрᚆޑނᅿᙦࡋࡋനଯǴځԛࣁܿࠄǵчǵՋࠄǴ ჹྣӚፓᒵޑങᅿኧ (чǺ131 ᅿǹՋࠄǺ65 ᅿǹܿࠄǺ201 ᅿǹᚆǺ 159ᅿ)Ǵᗨฅᚆᕛނᅿኧ٠ߚനଯǴӢࣁᕴ׀ኧၨեޑጔࡺԶӧނᅿᙦࡋ
ࡰଯܭځдӦ (კ 4)ǹӭኬ܄ࡰБय़Ǵᚆᕛᆶ 2003 Ϸ 2004 ԃፓϐ чᆶࠄϺฅᕛዬௗ߈ (ЦǴ2004)Ǵӧဂᆫಔԋᖿ߈ᛙۓǴځԛࣁܿࠄǴ ԶчᆶՋࠄᕛ߾ୃեǴᆶ Shao et al. (1997) КၨϺฅᕛӭኬ܄നଯޑෳઠр
ӧᏜޑ่݀ౣԖৡ౦Ƕӭኬ܄ࡰڙډঁᡏኧᆶނᅿኧޑቹៜǴނᅿኧຫӭǴ ӭኬ܄ΨຫଯǴฅԶऩԖϿኧങᅿޑঁᡏኧࡐӭǴࠅ٬ӭኬ܄ࡰफ़եǶԜ
วғӧчᕛዬᆶᐱҥᕛǴӧങᅿኧৡ౦όεޑݩΠǴᕴ׀ኧၨεޑᐱҥ ᕛӧӭኬ܄ࡰࠅᇽܭчᕛዬ (၏Ǵ2003)Ƕᐱҥᕛ܈ΓπങᕛޑᆫങਏᔈǴ рϿኧങᅿεໆᆫޑຝǴӭኬ܄ࡰΨӢԜफ़եǴӢԜӧှ᠐Ϻฅᕛዬᆶ Γπങᕛӭኬ܄ਔᔈᙣǹ֡ϬࡋБय़ǴࡰрᚆᕛങᅿӧኧໆϩѲന֡ϬǴ ځԛࣁܿࠄᆶՋࠄǴԶч࣬ၨܭќѦΟౣեǴځ่݀ᆶӭኬ܄ࡰᜪ՟Ǵՠ җܭՋࠄᕛނᅿኧၨեǴӧ֡ϬࡋߡКчٰளଯǶ
ӧѤੇୱύǴନΑᚆෳઠᕴ׀ኧදၹόଯѦǴќѦΟрεໆങᜪ ޑᆫ (კ 5)ǹځ໔׀ኧࡐӭޑങᅿӧчЬाҗϺޞ᜶ࣽǵഒ᜶ࣽکҡᢙࣽങᜪ
܌ᄬԋǹՋࠄ߾аϺޞ᜶ࣽǵഒ᜶ࣽλࠠങᜪϷߎᢙࣁЬǹܿࠄᕛ߾аҡᢙ
ࣽǵϺޞ᜶ࣽǵ〝ࣽǵᔕߎࣽǵഒ᜶ࣽࣁЬǹᚆϩǴԖίଫкߎ᜶ (ᔕ ߎ᜶ࣽ) ӧλౚෳઠрǴϐѦޑങᅿӧ׀ኧ٠ؒԖܴᡉଯঢ়ǶӧϺฅᕛ ޑࣴزύǴഒ᜶ǵໜᓐങࣁதـޑᓬ༈ނᅿǹ࣬ჹϐΠǴӧΓπӦύၨࣁதـ ޑ߾ࢂᔕߎ᜶ᆶᠣ᜶ (Wen et al. 2010)ǶӧҁࣴزύǴᠣ᜶ӧᚆӦኧໆၨ
ӭǴᔕߎ᜶߾ӧܿࠄکᚆᕛεໆрǶчੇୱങᕛޑങᜪᕴ׀ኧᆶܿ
ࠄᕛᜪ՟ǴԶܿࠄᕛޑғނໆၨଯǴЬाࢂӢࣁᆫΑᡏࠠၨεޑᒯ׀᜶
(Prionurus scalprum) کѤᚊങ(Pomadasys quadrilineatus)Ƕᚆޑᕴ׀ኧၨեǴ
ோӧғނໆԛܭܿࠄᕛǴځύӾવᐪങ (Platax teira) کϤሷങ (Naso hexacanthus) ޑଅࡐεǶӧՋࠄੇୱǴӢϺޞ᜶ᆶഒ᜶ޑᡏࠠၨλǴѬॺჹങ ᕛޑᡏങᜪғނໆޑଅ٠όεǶ
คፕӧങᜪޑဂᆫಔԋǵဂᆫࡰ܈ࢂᕴ׀ኧᆶғނໆǴӧѤঁੇୱ໔ࣣ
Ԗܴᡉৡ౦Ǵёـᕛᒧ֟ޑ٣πբߚதख़ाǴىа،ۓᕛࡕങᜪဂᆫޑಔ ԋ่ᄬ (Bohnsack and Sutherland 1985)Ƕ
4.2 όӕᕛࠠჹങᜪဂᆫޑቹៜ
ҁࣴزӅፓϖᅿόӕᜪࠠޑΓπങᕛǴхࡴНݝᕛǵႝఎᕛǵᒳ៓ᕛǵᅕ
ಭᕛǵैᝮᕛǴନΑᕛࠠҁي፦ޑৡ౦ϐѦǴНݝᕛکᒳ៓ᕛࣁߐीޑ Γπ่ᄬᡏǴᕛᡏޑᄬࠠૈႣӃϒа،ۓǶᕛᡏ߄य़ϾሜᆶࢰҤޑελჹܭό ӕᡏࠠޑങԖόӕޑቹៜǴᡏࠠλޑങୃӳၧᙒӧλϾࢰύǹᡏࠠัε܈౽ૈ
ΚமޑങύჹܭϾ৩ελΞԖόӕሡ (Hixon and Beets 1989; Wilson et al. 2007)Ǵ
٬ҔНݝᕛ܈ᒳ៓ᕛޑӳೀߡࢂૈଞჹҞങᅿႣӃޑᄬࠠीǶНݝᕛҁ ي܄፦ᛙۓǴё୴᠄௨ӈǴฅԶߏਔ໔ڙډੇࢬߟᇑΠ፦Ԗёૈှǹᒳ៓ᕛ ޑҥᡏޜ໔εǴ٬Ҕԃज़ၨߏǶฅԶٿޣख़ໆၨεǴࡼπᜤࡋଯǴЪ٬Ҕᒳ៓ԋ ҁၨଯǶၨ࣪ޑբݤࣁ٬ҔΒԛǴஒቲకޑႝጕఎϪപǵᇙԋႝ
ఎᕛǴ܈ࢂஒၸೀޑቲకಭଫǵैᝮ؈ܫΕੇύ (၏کቅǴ2011)ǶԶӧόӕ ᕛࠠϐ໔ࢂցӵӕ Walker et al. (2002) ளډؒԖৡ౦ޑ่݀Ǵӧҁࣴزύаဂᆫ่
ᄬǵဂᆫࡰǵᕴ׀ኧᆶғނໆٰКၨǶ
ঁձଞჹόӕᕛǴа ANOSIM Кၨᕛࠠৡ౦ޑ่݀ᡉҢǴӧчᆶՋࠄᕛ
ǴဂᆫಔԋؒԖܴᡉৡ౦Ǵќӧܿࠄᕛޑैᝮᕛᆶᒳ៓ᕛǵᚆᕛޑႝఎ ᕛᆶᒳ៓ᕛӧဂᆫ่ᄬԖᡉৡ౦ (߄ 3Ǵ4)ǶӚੇୱӧނᅿᙦࡋ (D)ǵӭ ኬ܄ (H’) Ϸ֡Ϭࡋ (J’) ΟᅿဂᆫࡰǴӧᕛࠠ໔ؒԖৡ౦ (߄ 7)Ƕ
ϩᡉҢчैᝮᕛғނໆεܭНݝᕛᆶᅕಭᕛǴᒳ៓ᕛғނໆΨε ܭНݝᕛᆶᅕಭᕛǴԶႝఎᕛғނໆӧෳઠ໔ޑৡ౦ၨεǴԜёૈᆶᕛޑՏ
܈ࢂᕛޑۭ፦Ԗᜢ (ӧځύԖ٤ങᕛࢂܫӧϺฅᕛ)ǶՋࠄᕛᅕಭᕛޑ ғނໆεܭНݝᕛǴ݅ᜐ (Ο) ᒳ៓ᕛᆶܽቧ (Β) ޑᒳ៓ᕛᆶғނໆ࣬ৡཱུεǴ Ԝёૈᆶܽቧ (Β) ۭᙟᇂԖᜢ (5.5%ǹ݅ᜐ (Ο) ࣁ 24~72%)Ƕᚆᕛႝ
ఎᕛӧᕴ׀ኧБय़Ǵεܭᒳ៓ᕛᆶैᝮᕛǴЬाӢӚႝఎᕛෳઠᒵډ 100ɴ200 ଫࠖМ౦நӓᠧ (Heteroconger hassi )ǴฅԶӧځӧғނໆޑଅ٠όεǴЪځ рᆶΓπങᕛᆶցၨค࣬ᜢǶٿ০ᒳ៓ᕛύрεໆޑӾવᐪങ (Platax teira)ǴᏤठᒳ៓ᕛෳઠޑғނໆрཱུଯॶǶ
чکܿࠄᕛैᝮᕛᆫങਏ݀ؼӳǴᔈᆶैᝮᕛҁي่ᄬፄᚇԖᜢǴЪҗ
ܭಭيᕛᡏࠟޔଯࡋǴܰ֎Ї߄ቫᆶۭޑങᅿǴ࣬ၨܭځдᕛࠠԖၨଯޑғ ނໆ (Lukens and Selberg 2004)ǶฅԶಭᝮޑ่ᄬڙډረ॥ቹៜޑำࡋόǴBell and Hall (1994) ᇡࣁ 50 ϦЁаభޑಭᕛܰڙډமਗ਼ረ॥ቹៜԶՏ౽Ƕӧᆘᆶ λౚޑैᝮᕛǴڙډӚᅿނ܄ޑߟᇑբҔǴεϩಭيςှᡏᘐǴᕛᡏ่
ᄬ࿗ТණѲǴӢԜӧᆫങਏ݀εѺשԌǶ
4.3 ങᜪဂᆫϩѲᆶᕉნӢηᜢ߯
BIO-ENVճҔόӕᕉნӢηಔӝीᆉᆶങᜪဂᆫޑ࣬ᜢ߯ኧǹCCA ߾ࢂஒങ ᜪဂᆫύޑނᅿനεᡂϯໆӧᕉნఊࡋևрٰǶٿᅿϩБݤޑ่ࣣ݀ࡰр ቹៜѤঁୱങᜪဂᆫಔԋৡ౦ޑᕉნӢηࣁጎࡋǵૈـࡋǵۭ፦ᜪࠠǴЪ CCA
่݀ࡰрᕴғނᙟᇂǵᝯᜪᆶ؇ᑈނࠆࡋჹങᜪဂᆫΨԖቹៜǶBriggs (1995) ᇡ ࣁғނӭኬ܄ᒿ۳ྕԶሀ෧ǹӧҁࣴزύǴങᜪဂᆫݮܿч-Ջࠄޑ ϪጕևࠄчٿεϩဂǴӧܿࠄᆶᚆᕛԖၨଯޑങᅿӭኬ܄ǴЬाӢࣁᕛᡏ
܌ӧՏڙډόӕޑࢩࢬس܌ቹៜǴёـጎࡋᆶࡋჹܭങᜪဂᆫ่ᄬڀԖख़ εޑቹៜǶΓࣴزᇡࣁྕࡋࢂቹៜങᜪဂᆫനЬाޑӢη (Bortone et al. 1994;
Shao et al. 1997; Ferreira et al. 2004)ǴਥᏵ୯ࣽੇࢩᏢߐၗύޑНЎᆶੇࢬ
ी่݀ǴѠڬൎੇୱ 30 ϦЁుӧহۑ (6~8 Д) НྕؒԖܴᡉৡ౦ǴҗܭϺǵ
ੇݩज़ڋǴፓਔ໔ύӧহۑаϷࡕٿঁДǴӢԜӧҁࣴزύǴྕࡋჹ ܭങᜪဂᆫޑቹៜ٠όܴᡉǶ
ૈـࡋ (Н፦మᅒࡋ) ᆶ؇ᑈނࠆࡋٿᕉნӢηڀԖॄ࣬ᜢޑᖿӛ (კ 9)ǹ
ԶقǴૈـࡋ٫ޑᕉნǴϿԖ؇ᑈނ୴ᑈǹૈـࡋৡޑᕉნǴ؇ᑈނ୴ᑈࠆ ࡋଯǶGodoy et al. (2002) วӧΓπങᕛങᜪဂᆫᆶૈـࡋևଯࡋ࣬ᜢǹ Cyrus and Blader (1987) ߾ᇡࣁᕉნషᐜࡋଯǴૈ෧ϿѴങਂ१ǶԶ؇ᑈނࠆ ࡋჹങᜪဂᆫࣁ໔ௗቹៜǴۭߕғނڙډ؇ᑈނޑቹៜ׳ࣗǴٯӵ؇ᑈނޑ
୴ᑈᏤठ࣑ྴ౾৲ǴࣗԿቹៜډځдคૉނޑޑߕ (Birrell et al. 2005ǹᔎǴ
2006)Ƕӧ CCA ޑ่݀ύǴᚆǵܿࠄᆶՋࠄᕛޑങᜪဂᆫᆶෳઠᒿૈـࡋɡ
؇ᑈނࠆࡋޑᕉნఊࡋԶϩѲӧᚈׇკǶ
ۭ፦ᜪࠠ߾ᆶૈـࡋɡ؇ᑈނࠆࡋޑᕉნఊࡋևᜪ՟ޑቹៜǴᚆᕛ
ۭ፦ᜪࠠа۟ዬࣁЬǴН፦మᅒǴϿ؇ᑈނ୴ᑈǹࣳݝۭ፦ޑՋࠄᕛǴН፦
షᐜǴ؇ᑈނ୴ᑈᝄख़Ƕ
ᝯᜪᙟᇂϷᕴғނᙟᇂࣁቹៜങᜪဂᆫޑԛाғނ܄ᕉნӢηǶᝯᜪᆶ
ۭғނҁيҭڙډځдᕉნӢη܌ቹៜǹFabricius et al. (2005) ᆶ McClanahan et al. (2007) ࡰрᝯᜪޑᙟᇂϷғނໆڙډᔼᎦᡶӭჲ܌ቹៜǴԶᝯᜪޑӀӝբҔ ਏΞᆶӀጕԖᜢǴుࡋຫుǴНᡏషᐜࡋຫଯǴӀӝբҔޑਏߡຫৡǶѠ
ڬᎁੇୱᔼᎦᡶϩѲҗύ୯ݮ۞Կዊሀ෧ (Zhang et al. 2007)ǴᏃᆅࠄҗܭᔼ ᎦᡶቚуϷ१ᝯ܄ങᜪ౽ନᏤठ࣬ᡂ (Chang and Tseng 2010)Ǵӧځдܿࠄᆶᚆ
Ӧ٠คޔௗᏵࡰрᔼᎦᡶޑቚуԋၨଯޑᝯᜪᙟᇂǶҗܭΓπങᕛ
ޑϩѲుࡋǴӧୱ໔٠คܴᡉৡ౦ǴӢԜܿࠄᆶᚆӦԖၨଯޑᝯᜪᙟᇂǴ ԜᔈᆶН፦ၨమᅒǵӀጕऀࡋଯԖᜢǶBaynes and Szmant (1989) ᇡࣁߕғނ ޑᙟᇂᆶނᅿӭኬ܄ڙډੇࢬޑம১ᆶ؇ᑈբҔԖᜢǴܿࠄǵᚆᕛၨଯޑ
ۭғނᙟᇂǴձࢂᘠ१܄ޑߕғނǴёૈᆶ೭ٿᕉნӢηԖᜢǶ
ᡏԶقǴӧቹៜങᜪဂᆫϩဂޑᕉნӢηύǴനЬाޑӭឦߚғނ܄ޑᕉ ნӢηǴԶۭғނ࣬ғނ܄ޑᕉნӢη߾ࣁቹៜങᜪဂᆫޑԛाӢηǴև
Ԝ่݀ёૈࣁғނ܄ᕉნӢη (ۭғނ) ҁيҭڙډӚᅿނ܄ᕉნӢηᆶ ങᜪޑਂ१ਏᔈ܌ቹៜǴЪԛޑፓǴങᜪᆶۭғނᙟᇂޑߏёૈ
ೀܭᄊѳᑽޑόӕਔ໔ᗺǴӢԜғނ܄ᕉნӢηᆶങᜪဂᆫޑ࣬ᜢ܄ߡόऩ ߚғނ܄ޑᕉნӢηܴᡉǶ
ҁࣴز٬Ҕޑж߄ങᅿόຬၸϖଫǴӧж߄܄ങᅿޑᒧऩૈӈΕ׳ӭ
ୱ܄ޑж߄ങᅿǴᔈૈቚуϩ่݀ޑᆒዴ܄ᆶё܄Ƕ
4.4 ങᜪဂᆫᆶ१܄ಔԋ
ӧঁങᜪဂᆫύǴങᅿӧ१܄ҭڀԖӭኬ܄ǶӧԖज़ޑёճҔၗྍΠǴ ғނ໔วғᝡݾຝǴ٠ॐ٬дॺϩଛ٬Ҕόӕޑၗྍ (Ross 1986)Ƕᙖҗϩ१
܄фૈဂޑಔԋǴૈᔅշךॺှ१ނᆛύૈໆᆶғނໆޑࢬ (Garrison and Link 2000b)Ƕӧۭғނᆶങᜪဂᆫޑ࣬ᜢ܄ࣴزύǴԖёૈрਂ१ޣᆶ१ ނև҅࣬ᜢǴΨԖёૈӢࣁਂ१ਏᔈΠǴਂ१ޣӭԶ१ނ෧ϿǴӢԶόܰளډ
ܴዴޑှញǶӢԜǴҁࣴزख़ӧϩКၨങᜪޑ१܄ಔԋǴᏵаෳόӕޑᕛ
ჹۓၗྍޑሡำࡋǶ
аӚ१܄ಔԋӧғނໆޑԭϩКٰ࣮Ǵчᕛаឪ१ۭคૉނޑങ ᜪࣁԜᓬ༈१܄фૈဂǹՋࠄᕛЬाύӧ१คૉނ१܄ک१ങ१܄ǹ
ܿࠄᕛаᝯ१܄ᆶ१ۭคૉނ՞εϩКٯǹᚆᕛ߾ࢂੌෞނ१
܄ᆶۭคૉނ१܄ၨଯǶ
ۭคૉނεᡏёϩࣁٿεᜪǺ౽܄ᆶڰ܄Ƕ౽܄คૉނ х֖Ҙෘᜪǵ೬ᡏނǴନΑӧ۟ᕛ୷፦ѦǴΨૈϩѲӧڬᎁࣳݝۭ፦ǹڰ
܄คૉނх֖࣑ྴǵऱឿᙝǵੇᓋǵੇᆟǴதߕӧ୲ฯޑ୷፦ (Ferreira et al. 2004)Ƕчᕛങᜪ१܄ύӧۭคૉނ१܄Ǵӧ௨ׇύԖҡ࣑
ྴᆶᛯ൙ޑᙟᇂᆶങᜪဂᆫ࣬ᜢǴՠ٠όૈж߄дॺࣁ೭٤ങᜪޑЬा१ނٰ
ྍǴёૈࣁ܌ୃӳޑ࣬ᜢǶӧᆶྕᕛޑࣴزύǴਂ१౽܄ۭ
คૉނޑങᜪࢂനЬाޑ१܄ᜪဂ (Ebeling and Hixon 1991; Jones et al. 1991)Ǵ
৲ӧчങᕛڬൎޑۭคૉނޑၗྍໆᔈ࣬ᙦǴБىаගٮ१ۭ
คૉނޑങᜪਂ१ǴόၸӧወНፓύܰեޑ౽܄คૉނǴ ӢԜځख़ा܄٠҂ӧᕉნӢηϩύᡉрٰǶ
ՋࠄᕛύᆫΑኧໆ࣬ӭޑഒ᜶ᆶϺޞ᜶ǴԶவ௨ׇϩύ٠คۭғ ނᆶങᜪဂᆫև࣬ᜢǴ೭٤λࠠങᜪޑϩѲёૈᆶᕛᡏගٮёᗉእޑ܌ԖᜢǴ Զ१ނ٠όࢂঁज़ڋӢηǶόၸǴ೭٤ᆫޑλࠠങᜪǴӕਔΨ֎ЇΑ१ങ१
܄ϷԺ१܄ങᜪӵಂ᜶ᆶҡඬǴӢԜՋࠄᕛύ१ങ१܄՞ғނໆޑԭϩКၨ
ځдӦٰளଯǶ
ܿࠄᕛғނໆԭϩКၨଯޑࣁۭคૉނ१܄ᆶᝯ१܄Ǵځύϩ х֖ᚇ१܄ǶFerreira et al. (2004) ᇡࣁᚇ१܄ޑങᜪϩѲӧጎࡋၨଯޑӦǴҗܭ १܄ၨڀቸ܄Ǵय़ჹۑ܄ޑᕉნᘋਔڀԖᓬ༈ǶӧҁੇୱങᕛύǴᚇ १܄ύғނໆଅനଯޑᒯ׀᜶ (Prionurus scalprum) ٠όڀԖଯጎࡋϩթǴЪӧ ௨ׇკύҭᆶᝯᜪޑ࣬ᜢ܄όଯǴӢԜۭคૉނёૈࣁځၨୃӳޑ१ނٰ
ྍǶ
ᚆᕛ१ੌෞނޑങᜪӧኧໆ܈ғނໆ܌՞ޑԭϩК࣬ଯǴԜԖ ౦ܭځдΟǶSheppard et al. (2009) ᇡࣁ१ੌෞނങᜪޑ१ނନΑҗࢩࢬவѦ ӦٰаѦǴϩٰԾܭᕛǴхࡴ࣑ྴӕᡏౢռǴ܈ࢂځдคૉނ
܈ങᜪ܌ញܫޑଛηǶԜѦǴዊࢬᆘߕ߈ڙډӦᆶࢩࢬᓸΚޑቹៜΠǴ
ੇୱрϲࢬǴ٬ளᔼᎦᡶቚуǴٰεໆޑੌෞғނǴᆫӭޑ१ੌෞ
ނങᜪӧԜ१ (णǴ2008)Ƕ
ᡏԶقǴӧΓπങᕛനЬाޑ१܄ᄬԋࣁۭคૉނ१܄ǴᆶӃ
ࣴزᜪ՟ (Khalaf and Kochzius 2002; Relini et al. 2002; Ferreira et al. 2004; Floeter et al. 2004)ǶԾᔼ܄ғᄊسӧܿࠄᆶᚆᕛၨёૈрǴӧ೭ٿҭதـ࣑ྴᙝ१
܄ᆶమዅ१܄ങᅿǴӧဂᆫޑ१܄่ᄬၨч܈ՋፄᚇǶ
4.5 ่ፕ
ၸങᜪဂᆫ่ᄬǵғނဂᆫࡰǵᕴ׀ኧᆶғނໆޑϩǴךॺวѤঁ
ങᕛӧӚঁҞޑᔠᡍύࣣևᡉৡ౦ǴӢԜВࡕଞჹӚঁෳઠޑᆫങਏ݀
ਔǴᔈᆶӕᕛϣങᜪဂᆫಔԋᜪ՟ޑෳઠ࣬КၨǴᗉխၠෳઠКၨਔڙډ ᕛ໔ޑৡ౦܄܌ቹៜǶ
ᕛࠠБय़ǴᗨฅӚғނဂᆫࡰޑϩύࣣคᢀჸډᕛࠠόӕޑৡ౦Ǵՠ
ࢂܿࠄᕛޑैᝮᕛᆶᒳ៓ᕛӧങᜪဂᆫಔԋڀԖৡ౦Ǵчᆶܿࠄᕛޑै
ᝮᕛങᜪғނໆ׳ࢂᡉଯܭځдᕛࠠǴԶځдᕛࠠ໔ޑৡ౦߾όܴᡉǶ
ӧቹៜങᜪဂᆫϩဂޑᕉნӢηύǴനЬाޑӭឦߚғނ܄ޑᕉნӢηǴٯ ӵᕛᡏޑՏ (ࡋᆶጎࡋ)ǵᕉნޑރݩ (ૈـࡋǵ؇ᑈނǵۭ፦ᜪࠠ) ǴԶۭ
ғނ࣬ғނ܄ޑᕉნӢη߾ࣁቹៜങᜪဂᆫޑԛाӢηǶ
१܄่ᄬޑϩᡉҢۭคૉނ१܄ࣁӚᕛЬाޑ१܄ᜪဂǹќՋࠄ ᕛӭԺ१܄ങᜪǵᚆᕛӭੌෞނ१܄ങᜪǹܿࠄϷᚆᕛᝯᜪᙟᇂ
ଯǴΨԖၨଯޑ१ᝯ܄ങᜪဂᆫǴ१࣑ྴᙝᆶమዅ१܄ޑങᜪҭதрǴ࣬ၨԶ قǴчᆶՋࠄᕛ१܄่ᄬޑಔԋ߾࣬ჹൂપǶฅԶ൩ᔮ܄ങᅿޑػǴ чᆶՋࠄᕛޑਏ݀ၨܴᡉǶࡺӧΓπങᕛޑೕჄᆶᆅǴە൩ܫΓ πങᕛޑҞޑόӕǴϩԵໆǶ
ҴǵୖԵЎ
Ц௵ܱǵቅ྆ᑫǵഋᓉ܃ǵ၏ᄪਦǴ2004ǴѠΓπങᕛޑਏຑǶѠڬᜐ
ੇୱΓπങᕛᡏೕჄࣴፕЎǶ၏ᄪਦጓǶύѧࣴزଣғނӭኬ܄
ࣴزύЈǴ77-94 ।
णӀᓪǴ2008Ǵੇࢩᕉნ䃲ፕ : ፋѠݮੇᕉნǶѠчѱǴѠՋਜ
ᐛӹǴ2008ǴፄᚇࡋᢀᗺΠϐന٫ϯޜ໔թǺΓπӦीᆶᔈҔǶࠄε ᏢҾᆅسᆅࣽᏢറγፕЎǴ100 ।
ഋণᖃǵ၏ᄪਦǵᔎܱስǴቅϘሎǴ2008ǴࡀܿϷѠܿੇୱΓπങᕛፓຑ
πբǶՉࡹଣၭہᅕᅕวीฝ 96 ԃࡋൂीฝය҃ൔǴ 596।
၏ᄪਦǵЦ௵ܱǵֻ݅၈ǵቅ྆ᑫǵഋᓉ܃ǵֺε൬ǵՖࡹǵ߉ࠧၲǴ2003Ǵ ѠڬᜐੇୱΓπങᕛϐᡏೕჄǶΐΜΒԃࡋՉࡹଣၭہᅕ
ہૼीฝՉԋ݀ൔǴ186 ।
၏ᄪਦǵЦ௵ܱǵቅ྆ᑫǵഋᓉ܃ǵֺε൬ǵ߉ࠧၲǵՖࡹǴ2004ǴѠڬᜐ
ੇୱΓπങᕛϐᡏೕჄ (Β)ǶΐΜΟԃࡋՉࡹଣၭہᅕہ
ૼीฝՉԋ݀ൔǴ425 ।
၏ᄪਦǵቅϘሎǴ2009ǴΓπങᕛᅕਏፓࣴزǶՉࡹଣၭہᅕ
98ԃࡋࣽמीฝࣴزൔǴ286 ।
၏ᄪਦǵቅϘሎǴ2010ǴΓπങᕛᅕਏፓϷёՉ܄ຑǶՉࡹଣၭہ
ᅕ 99 ԃࡋࣽמीฝࣴزൔǴ231 ।
၏ᄪਦǵቅϘሎǴ2011ǴΓπങᕛֹӄЋнǶύѧࣴزଣғނӭኬ܄ύЈǴ42
।
ᔎܱስǴ2006Ǵংᡂᎂჹך୯ϐፂᔐᆶፓౣࣴز-ηीฝΟǺংᡂᎂᆶ ౦தჹך୯ੇୱ࣑ྴᕛғނဂᆫϐፂᔐຑϷӢᔈౣࣴزǶ94 ԃࡋȨᕉ
ߥ/୯ࣽޜԦٛڋࣽࣴӝբीฝȩԋֹ݀ൔǴ46 ।Ƕ Angel A, Ojeda FP (2001) Structure and trophic organization of subtidal fish
assemblages on the northern Chilean coast: the effect of habitat complexity.
Marine Ecology Progress Series 217: 81-91
Ardizzone GD, Somaschini A, Belluscio A (1997) Biodiversity of European artificial reefs. In: Jensen AC (ed) European Artificial Reef Research, Proceedings of the 1st EARRN Conference, Ancona, Italy, March 1996, pp 39-59
Arias-González JE, Done TJ, Page CA, Cheal AJ, Kininmonth S, Garza-Párez JR (2006) Towards a reefscape ecology: relating biomass and trophic structure of fish assemblages to habitat at Davies Reef, Australia. Marine Ecology Progress Series 320: 29-41
Baynes TW, Szmant AM (1989) Effect of current on the sessile benthic community structure of an artificial reef. Bulletin of Marine Science 44: 545-566
Bell M, Hall WJ (1994) Effects of Hurricane Hugo on South Carolina's marine artificial reefs. Bulletin of Marine Science, 55 2: 836-847
Bellwood DR, Wainwright PC, Fulton CJ, Hoey A (2002) Assembly rules and functional groups at global biogeographical scales. Functional Ecology 16:
557-562
Birrell CL, McCook LJ, Willis BL (2005) Effects of algal turfs and sediment on coral settlement. Marine Pollution Bulletin 51: 408-414
Bohnsack JA (1989) Are high densities of fishes at artificial reefs the result of habitat limitation or behavioral preference? Bulletin of Marine Science 44: 631-645 Bohnsack JA, Sutherland DL (1985) Artificial reef research: a review with
recommendations for future priorities. Bulletin of Marine Science 37: 11-39 Bortone SA, Martin T, Bundrick CM (1994) Factors affecting fish assemblage
development on a modular artificial reef in a northern Gulf of Mexico estuary.
Bulletin of Marine Science 55: 319-332
Bortone SA, Samoilys MA, Francour P (2000) Fish and macroinvertebrate evaluation methods. In: Seaman W (ed) Artificial Reef Evaluation: With Application to Natural Marine Habitats. CRC Press, Boca Raton, Florida, pp 127-164 Briggs JC (1995) Global biogeography. Elsevier, Amsterdam
Brock RE (1982) A critique of the visual census method for assessing coral reef fish populations. Bulletin of Marine Science 32: 269-276
Brotto DS, Krohling W, Zalmon IR (2006) Fish community modeling agents on an artificial reef on the northern coast of Rio de Janeiro-Brazil. Brazilian Journal of Oceanography 54: 205-212
Bull AS, Kendall JJ (1994) An indication of the process: offshore platforms as artificial reefs in the Gulf of Mexico. Bulletin of Marine Science, 55 55: 1086-1098 Chang JS, Tseng CC (2010) Effects of recent ecological events on the distribution and
growth of macroalgae in marine waters around Taiwan. Bulletin of Fisheries Research Agency 32: 11-17
Charbonnel E, Serre C, Ruitton S, Harmelin JG, Jensen A (2002) Effects of increased habitat complexity on fish assemblages associated with large artificial reef units (French Mediterranean coast). ICES Journal of Marine Science 59: S208-S213 Chen JP, Shao KT, Ho LT, Chen LS, Kao PH, Wu YY (1992) Fish fauna and their
geographical distribution in the coastal waters around Hsiao-liu-chiu, southwestern Taiwan. Acata Zoologica Taiwanica 3: 105-134
Clarke KR (1993) Non-parametric multivariate analyses of changes in community structure. Australian Journal of Ecology 18: 117-143
Clarke KR, Gorley RN (2006) PRIMER v6: User manual/tutorial. PRIMER-E,
Plymouth, UK
Cole AJ, Pratchett MS, Jones GP (2008) Diversity and functional importance of coral feeding fishes on tropical coral reefs. Fish and Fisheries 9: 286-307
Cyrus DP, Blaber SJM (1987) The influence of turbidity on juvenile marine fishes in estuaries. Part 2. Laboratory studies, comparisons with field data and
conclusions. Journal of Experimental Marine Biology and Ecology 109: 71-91 Ebeling AW, Hixon MA (1991) Tropical and temperate reef fishes: comparison of
community structure. In: Sale PF (ed) The ecology of fishes on coral reefs.
Academic Press, San Diego, CA, pp 509-563
Fabricius K, De'ath G, McCook L, Turak E, Williams DMB (2005) Changes in algal, coral and fish assemblages along water quality gradients on the inshore Great Barrier Reef. Marine Pollution Bulletin 51: 384-398
Fast DE, Pagan FA (1974) Comparative observations of an artificial tire reef and natural patch reefs off southwestern Puerto Rico. In: Colunga L, Stone R (eds) Artificial Reef Conference, Texas A&M University, pp 49-50
Ferreira CEL, Floeter SR, Gasparini JL, Ferreira BP, Joyeux JC (2004) Trophic structure patterns of Brazilian reef fishes: a latitudinal comparison. Journal of Biogeography 31: 1093-1106
Ferreira CEL, Gonçalves JEA (2006) Community structure and diet of roving herbivorous reef fishes in the Abrolhos Archipelago, south western Atlantic.
Journal of Fish Biology 69: 1533-1551
Ferreira CEL, Gonçalves JEA, Coutinho R (2001) Community structure of fishes and habitat complexity on a tropical rocky shore. Environmental Biology of Fishes 61: 353-369
Fitzhardinge RC, Bailey-Brock JH (1989) Colonization of artificial reef materials by
corals and other sessile organisms. Bulletin of Marine Science 44: 567-579 Floeter SR, Ferreira CEL, Dominici-Arosemena A, Zalmon IR (2004) Latitudinal
gradients in Atlantic reef fish communities: trophic structure and spatial use patterns. Journal of Fish Biology 64: 1680-1699
Gallaway BJ, Lewbel GS (1982) The ecology of petroleum platforms in the
northwestern Gulf of Mexico: a community profile, FWS/OBS-82/27, Open File Report 82-03. USFWS Office of Biology Services, Washington, DC
Garrison LP, Link JS (2000a) Dietary guild structure of the fish community in the Northeast United States continental shelf ecosystem. Marine Ecology Progress Series 202: 231-240
Garrison LP, Link JS (2000b) Fishing effects on spatial distribution and trophic guild structure of the fish community in the Georges Bank region. ICES Journal of Marine Science: Journal du Conseil 57: 723-730
Godoy EAS, Almeida TCM, Zalmon IR (2002) Fish assemblages and environmental variables on an artificial reef north of Rio de Janeiro, Brazil. ICES Journal of Marine Science 59: S138-S143
González-Gándara C, Membrillo-Venegas N, Nuñez-Lara E, Arias-González JE (1999) The relationship between fish and reefscapes in the Alacranes Reef, Yucatan, Mexico: a preliminary trophic functioning analysis. Vie et milieu 49: 275-286 Guerin AJ (2009) Marine ommunities of North Sea offshore platforms, and the use of
stable isotopes to explore artificial reef foodwebs. Faculty of Enginering Science and Mathematics, School of Ocean and Earth Science, University of
Southampton, Ph.D. Thesis
Hixon MA, Beets JP (1989) Shelter characteristics and Caribbean fish assemblages:
experiments with artificial reefs. Bulletin of Marine Science 44: 666-680
Honório PPF, Ramos RTC, Feitoza BM (2010) Composition and structure of reef fish communities in Paraíba State, north eastern Brazil. Journal of Fish Biology 77:
907-926
Hueckel GJ, Buckley RM (1989) Predicting fish species on artificial reefs using indicator biota from natural reefs. Bulletin of Marine Science 44: 873-880 Jan RQ, Liu YH, Chen CY, Wang MC, Song GS, Lin HC, Shao KT (2003) Effects of
pile size of artificial reefs on the standing stocks of fishes. Fisheries Research 63:
327-337
Jennings S, Grandcourt EM, Polunin NVC (1995) The effects of fishing on the diversity, biomass and trophic structure of Seychelles' reef fish communities. Coral Reefs 14: 225-235
Jennings S, Polunin NVC (1996) Effects of fishing effort and catch rate upon the structure and biomass of Fijian reef fish communities. Journal of Applied Ecology 33: 400-412
Jensen AC, Collins KJ, Lockwood APM (2000) Current issues relating to artificial reefs in European seas. In: Jensen AC, Collins KJ, Lockwood APM (eds) Artificial Reefs in European Seas. Kluwer Academic Publishers, Dortrecht, The
Netherlands, pp 489-499
Jones GP, Ferrel DJ, Sale PF (1991) Fish predation and its impact on the invertebrates of coral reefs and adjacent sediments. In: Sale PF (ed) The ecology of fishes on coral reefs. Academic Press, San Diego, CA, pp 156-179
Kaiser MJ (2006) The Louisiana artificial reef program. Marine Policy 30: 605-623 Khalaf MA, Kochzius M (2002) Changes in trophic community structure of shore fishes
at an industrial site in the Gulf of Aqaba, Red Sea. Marine Ecology Progress Series 239: 287-299
Leitão F, Santos MN, Monteiro CC (2007) Contribution of artificial reefs to the diet of the white sea bream (Diplodus sargus). ICES Journal of Marine Science 64:
473-478
Lepš J, Šmilauer P (2003) Multivariate analysis of ecological data using CANOCO.
Cambridge University Press, Cambridge, UK.
Lukens RR, Selberg C (2004) Guidelines for marine artificial reef materials. Compiled by the Artificial Reef Subcommittees Atlantic and Gulf States Marine Fisheries Commission, pp 198
Masuda R, Shiba M, Yamashita Y, Ueno M, Kai Y, Nakanishi A, Torikoshi M, Tanaka M (2010) Fish assemblages associated with three types of artificial reefs: density of assemblages and possible impacts on adjacent fish abundance. Fishery
Bulletin 108: 162-173
Matthews KR (1985) Species similarity and movement of fishes on natural and artificial reefs in Monterey Bay, California. Bulletin of Marine Science 37: 252-270 McClanahan TR, Carreiro-Silva M, DiLorenzo M (2007) Effect of nitrogen,
phosphorous, and their interaction on coral reef algal succession in Glover's Reef, Belize. Marine Pollution Bulletin 54: 1947-1957
Moreau S, Péron C, Pitt KA, Connolly RM, Lee SY, Meziane T (2008) Opportunistic predation by small fishes on epibiota of jetty pilings in urban waterways. Journal of Fish Biology 72: 205-217
Muñoz AA, Ojeda FP (1997) Feeding guild structure of a rocky intertidal fish assemblage in central Chile. Environmental Biology of Fishes 49: 471-479 Nakamura M (1985) Evolution of artificial fishing reef concepts in Japan. Bulletin of
Marine Science 37: 271-278
O'Leary E, Hubbard T, O'Leary D (2001) Artificial Reefs Feasibility Study. Coastal