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2025-08-18 SMA-03-000007 Testimony Maki Morinoue
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Item #4 Scott Church and John Totah (Formerly Hale Pacifica LLC) (SMA 03-000007)
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2025-08-18 SMA-03-000007 Testimony Maki Morinoue
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a interventions of land-based stressors44.Management strategies that <br /> 0.30 leverage such policies to help mitigate coastal runoff,particularly in <br /> 0.25 urban areas,may support increased coral survival during severe marine <br /> 4 heatwaves. <br /> ID <br /> P 0.20 We also found thattotal fish biomass and scraper biomass were impor- <br /> ° tant factors in our models(Extended Data Table2).Healthyfish popu- <br /> 0 0.15 lations provide numerous reef-scale ecosystem functions29,including <br /> o some species releasing beneficial nutrient subsidies that increasecoral <br /> a 0.10 thermal tolerance45.Scrapers remove fast-growing algal turfs that could <br /> otherwise outcompete and overgrow stress-compromised corals30 By <br /> 0.051 <br /> Low Moderate comparison to phytoplankton biomass and coastal runoff,the slopes <br /> 0 5 10 15 20 25 30 35 40 45 50 of the relationships between total fish biomass and scraper biomass <br /> Cover of reef-building organisms(%) with heat-driven coral loss Were Weak(Extended Data Fig.4).Intense <br /> b Resource Probability marine heatwaves can cause severecoral mortality even on highly pro- <br /> management scenario Low Moderate High tected,uninhabited reefswith intact fish population s46,suggestingthat <br /> Initial condition Q 0.83 0.17 0.02 extreme heat stress may simplyoverwhelm the functional roles of reef <br /> Sea-based only Q 0.30 0.70 0.14 fish over shorttime scales.However,abundant fish populations,in par- <br /> Land-based only Q 0.17 0.83 0.26 ticular herbivores,can supportcoral reef recovery potential following <br /> Integrated land-sea Q 0.02 0.98 0.80 disturbance 2.Understanding whether this positive relationship holds <br /> across gradients in land-based impacts is key for supporting targeted <br /> og oa o� 06 05 06 810 o�� fisheries management in coastal marine ecosystems. <br /> 640 <br /> Coral reefs four years postdisturbance <br /> t 490 <br /> o The dominant reef-builders in tropical coral reef ecosystems are <br /> 360 oa hard corals and crustose coralline algae21.Crustose coralline algae <br /> ° are encrusting calcifying algae that fuse the reef framework together <br /> 5250 05 and promote coral growth by serving as a successional prerequisite for <br /> 6 160 06 coral recruitment and suppressing competitive fleshy algae 21.Given <br /> that coral cover can take a decade or more to recover to prebleaching <br /> N 90 0- level s41,assessing the total cover of reef-building organisms(hard <br /> 40 coral+crustosecora Ili nealgae)is more indicative of coral reef recovery <br /> potential following disturbance.Our surveys four years following the <br /> 10 2015 marine heatwave found that reef-builder cover ranged from 3.4 <br /> 0 <br /> 111110011 to 51.9%(mean of 24.3%±1.7 s.e.;n=55;Fig.4a).Critically,there were <br /> 25 50 75 100 125 150 175 200 225 250 275 different reefs with high(more than or equal to the 75th percentile)and <br /> „4111l Scraper biomass(kg hal) 41864 low(less than or equal to the 25th percentile)reef-builder cover before <br /> Fig.4 1 Local management scenarios thatsupport coral reef persistence and after the marine heatwave.Nearly two-thirds of reefs with high <br /> four years postdisturbance.a,Percentage cover ofreef-building organisms reef-builder cover in 2019 did not support such levels ofcover before <br /> (hard coral+crustose coralline algae)among reefs surveyed(n=55)in 2019, the marine heatwave.Similarly,we observed a more than 40%change <br /> four years following the marine heatwave.colours represent low(<-25th in the location of reefs with low reef-builder cover between 2015 and <br /> percentile),moderate(>25th and<75th percentile)or high(>-75th percentile) 2019.This reshuffling of reefs in terms of relative reef-builder cover <br /> cover.b,Probability oflow,moderate or high cover ofreef-builders shown in suggested differential coral reef persistence in the years following <br /> relation to variations inscraperbiomassand wastewater pollution.Example severe heat stress. <br /> scenarios show that simultaneously decreasing wastewater pollution We used an ordinal logistic regression framework to identify the <br /> and increasing scraper biomass results in afargreater probability ofhigh local land-sea human impacts and environmental factors that best <br /> reef-builder cover(scenario'C')than achievingeither management scenario in supported coral reefpersistence in theyears following the 2015 marine <br /> isolation(scenariosA'and'B').The upper(250kgha')and lower(30kgha') heatwave.Decreased wastewater pollution and increased scraper <br /> management scenarios for scraper biomass represented the 92nd and 36th <br /> biomass were the most important and significant(P<0.05)in pre- <br /> percentiles,respectively.We specifically chose250 kg ha-'as it approximates <br /> the long-term mean(2003-2019;n=17)scraper biomass inKealakekuaBay,a dictingwhetherareefhadrelativelyhigherreefbuildercoverfour <br /> marineprotected area in our study region where no fishing has been allowed years postdisturbance(Extended Data Table3).Pollution from human <br /> since1969(Supplementary Fig.11).Similarly,the upper(600,0001 ha-')and waste affects coastal marine ecosystems glObally48and is especially <br /> lower(2,5001h')management scenarios chosen for wastewater pollution harmful to corals from untreated sources,such as septic tanks and <br /> represented the 95th and 36th percentiles ofthe 2019 distribution, cesspools,which are both common in Hawai'i49.Consequently,high <br /> respectively(Supplementary Fig.12).Probability values and lineswere derived concentrations oftoxins and pathogens]each into coastal waters that <br /> from the top model from ordinal logistic regression modelling(Extended Data increase coral disease,reduce coral growth and reproduction,and <br /> Table3,Methodsand Supplementary Information).Coloursfor low,moderate increase coral susceptibility to bleaching42.These negative impacts <br /> and high in bare the same as those in a.See Extended Data Table lforfu111istof on coral persistence aretherefore much reduced in areas ofdecreased <br /> local land-sea human impacts and environmental factors included in the wastewater pollution.Scrapers reveal bare substrate as they feed and <br /> analysis,includingthose removed that were highly correlated(r>0.7,Methods facilitate the settlement,growth and survival ofcrustose coralline <br /> and Supplementary Fig.8).See Supplementary Fig.9for predictor variable algae and corals following acute disturbance30.Beyond these top-down <br /> distributions. effects on benthic condition,bottom-up effects of improved habitat <br /> quality could be contributing to the positive relationshipwe observed <br /> between scraper biomass and higher reef-builder cover.Parrotfish are <br /> the dominant scrapers in Hawai'i,and typically have home ranges of <br /> 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