Skip to main content

An official website of the United States government

Here’s how you know

Official websites use .gov
A .gov website belongs to an official government organization in the United States.

Secure .gov websites use HTTPS
A lock ( Lock Locked padlock ) or https:// means you’ve safely connected to the .gov website. Share sensitive information only on official, secure websites.

NCA5 Logo
    • About This Report
    • Guide to the Report
    • Report Credits
    • Companion Podcast
    • Additional Resources
    • About this Report
    • Guide to this Report
    • OVERVIEW
    • Physical Science
    • 2. Climate Trends
    • 3. Earth Systems Processes
    • National Topics
    • 4. Water
    • 5. Energy
    • 6. Land
    • 7. Forests
    • 8. Ecosystems
    • 9. Coasts
    • 10. Oceans
    • 11. Agriculture
    • 12. Built Environment
    • 13. Transportation
    • 14. Air Quality
    • 15. Human Health
    • 16. Indigenous Peoples
    • 17. International
    • 18. Complex Systems
    • 19. Economics
    • 20. Social Systems and Justice
    • Regions
    • 21. Northeast
    • 22. Southeast
    • 23. US Caribbean
    • 24. Midwest
    • 25. Northern Great Plains
    • 26. Southern Great Plains
    • 27. Northwest
    • 28. Southwest
    • 29. Alaska
    • 30. Hawai'i and US-Affiliated Pacific Islands
    • Responses
    • 31. Adaptation
    • 32. Mitigation
    • Focus On
    • F1. Compound Events
    • F2. Western Wildfires
    • F3. COVID-19 and Climate Change
    • F4. Risks to Supply Chains
    • F5. Blue Carbon
    • Appendices
    • A1. Process
    • A2. Information Quality
    • A3. Scenarios and Datasets
    • A4. Indicators
    • A5. Glossary

    • All Figures
    • All Key Messages
    • View All Report Downloads
    • Download Full Chapter PDF
    • Download Chapter Handout
    • Download Chapter Figures (.zip)
    • Download Chapter Presentation Package
    • Descargar en Español
  • Art × Climate
  • NCA Atlas
  • EN ESPAÑOL
Hawai'i & USAPI
i

Thumbnail and enlarged maps of the US show the National Climate Assessment Hawaiʻi and US-Affiliated Pacific Islands region highlighted in dark blue. The region comprises the state of Hawaiʻi and the following US-Affiliated Pacific Islands: the Commonwealth of the Northern Mariana Island; the unincorporated territories of American Sāmoa, Guam, and the Pacific Remote Islands; and the following Freely Associated States: the Federated States of Micronesia, the Republic of the Marshall Islands, and the Republic of Palau. Light blue shading around the islands indicates exclusive economic zones.

Fifth National Climate Assessment
30. Hawai'i and US-Affiliated Pacific Islands

  • SECTIONS
  • Introduction
  • 30.1. Food and Water
  • 30.2. Human Health
  • 30.3. Built Environment
  • 30.4. Ecosystems and Biodiversity
  • 30.5. Indigenous Knowledge
  • Traceable Accounts
  • References
Previous Chapter
View All Figures
Next Chapter
Climate change—especially sea level rise, altered rainfall patterns, and rising ocean and air temperatures—impairs access to clean water and healthy food, undermines human health, threatens cultural resources and the built environment, exacerbates inequities, and disrupts economic activity and diverse ecosystems in Hawaiʻi and the US-Affiliated Pacific Islands. Adaptation efforts that build upon community strengths and center local and Indigenous Knowledge systems improve resilience.

INTRODUCTION

Moananuiākea, Hawaiian for the Pacific Ocean, connects a diverse group of island peoples who share reciprocal and spiritual relationships with the lands, waters, natural resources, and cultures of the region. Indigenous Knowledge systems derived from thousands of years of stewardship and underlying observations have sustained Pacific Islanders, as evidenced in the cultural practices of seafaring,1 canoe building, agroforestry (a farming system that includes trees),2,3,4,5 harvesting fish and other marine life,6,7,8 traditional medicine,9 and managing water.10

Authors
Federal Coordinating Lead Author
Mari-Vaughn V. Johnson, US Geological Survey, Pacific Islands Climate Adaptation Science Center
Chapter Lead Author
Abby G. Frazier, Clark University, Graduate School of Geography
Chapter Authors
Lucas Berio Fortini, US Geological Survey, Pacific Island Ecosystems Research Center
Christian P. Giardina, USDA Forest Service, Institute of Pacific Islands Forestry
Zena N. Grecni, Arizona State University, Pacific Research on Island Solutions for Adaptation (RISA)
Haunani H. Kane, Arizona State University
Victoria W. Keener, Arizona State University, Pacific Research on Island Solutions for Adaptation (RISA)
Romina King, University of Guam, Pacific Islands Climate Adaptation Science Center
Richard A. MacKenzie, USDA Forest Service, Institute of Pacific Islands Forestry
Malia Nobrega-Olivera, University of Hawaiʻi at Mānoa, Hawaiʻinuiākea School of Hawaiian Knowledge
Kirsten L. L Oleson, University of Hawaiʻi at Mānoa, Department of Natural Resources and Environmental Management
Christopher K. Shuler, University of Hawaiʻi, Water Resources Research Center
Ann K. Singeo, Ebiil Society
Curt D. Storlazzi, US Geological Survey, Pacific Coastal and Marine Science Center
Richard J. Wallsgrove, University of Hawaiʻi at Mānoa, William S. Richardson School of Law
Phoebe A. Woodworth-Jefcoats, NOAA Fisheries, Pacific Islands Fisheries Science Center
Contributors
Technical Contributors
Malia K. H. Akutagawa, University of Hawaiʻi at Mānoa, Hawaiʻinuiākea School of Hawaiian Knowledge
Rosanna A. Alegado, University of Hawaiʻi at Mānoa
Kristen C. Alkins, US Geological Survey, Pacific Coastal and Marine Science Center
Marie Auyong, NOAA Office for Coastal Management
John I. Borja, University of Guam, Pacific Islands Climate Adaptation Science Center
Laura Brewington, Arizona State University
Jeff Burgett, US Fish and Wildlife Service
Janice E. Castro, NOAA Office for Coastal Management
Sandra P. Chang, University of Hawai‘i at Mānoa
Patrick L. Colin, Coral Reef Research Foundation
Catherine A. Courtney, Tetra Tech Inc.
Laxmikant Dhage, University of Hawai'i at Mānoa
Diana Felton, Hawaiʻi Department of Health
Patricia Fifita, Oregon State University
L. Kealoha Fox, Institute for Climate and Peace
Kathleen S. Friday, USDA Forest Service
Scott J. Glenn, Hawaiʻi State Energy Office
Rodney L. Itaki, Pohnpei Department of Health & Social Services
L. Alex Kahl, NOAA Fisheries, Pacific Islands Regional Office
Heather Kerkering, US Geological Survey, Pacific Islands Climate Adaptation Science Center
Elizabeth Kiefer, University of Hawaiʻi, John A. Burns School of Medicine
Kelli A. Kokame, University of Hawaiʻi at Mānoa, John A. Burns School of Medicine
Natalie Kurashima, Kamehameha Schools
Dennis A. LaPointe, US Geological Survey, Pacific Island Ecosystems Research Center
Scott Laursen, Pacific Islands Climate Adaptation Science Center
Carlotta A. Leon Guerrero, Office of the Governor of Guam
Roseo Marquez, Micronesia Conservation Trust
Stephen E. Miller, US Fish and Wildlife Service, Pacific Islands Office
Tomoaki Miura, University of Hawaiʻi at Mānoa
Kanoe Morishige, NOAA Papahānaumokuākea Marine National Monument
Michael Parke, NOAA Pacific Islands Fisheries Science Center
Elliott W. Parsons, University of Hawai‘i at Mānoa, Sea Grant College Program
Kalani Quiocho Jr., NOAA National Ocean Service, Office of National Marine Sanctuaries
Laurie J. Raymundo, University of Guam Marine Laboratory
Nicole Read, Duke University
Bradley M. Romine, University of Hawai‘i at Mānoa, Pacific Islands Climate Adaptation Science Center
Clay Trauernicht, University of Hawaiʻi at Mānoa, Department of Natural Resources and Environmental Management
Yinphan Tsang, University of Hawaiʻi at Mānoa, Department of Natural Resources and Environmental Management
Colette C.C. Wabnitz, University of British Columbia, Institute for the Oceans and Fisheries
Matthew J. Widlansky, University of Hawai‘i at Mānoa, School of Ocean and Earth Science and Technology
Myeong-Ho Chris Yeo, University of Guam, Water and Environmental Research Institute
Review Editor
Carolyn V. Balk, Federal Emergency Management Agency
USGCRP Coordinators
Allyza R. Lustig, US Global Change Research Program / ICF
Christopher W. Avery, US Global Change Research Program / ICF
Recommended Citation

Frazier, A.G., M.-V.V. Johnson, L. Berio Fortini, C.P. Giardina, Z.N. Grecni, H.H. Kane, V.W. Keener, R. King, R.A. MacKenzie, M. Nobrega-Olivera, K.L.L. Oleson, C.K. Shuler, A.K. Singeo, C.D. Storlazzi, R.J. Wallsgrove, and P.A. Woodworth-Jefcoats, 2023: Ch. 30. Hawai‘i and US-Affiliated Pacific Islands. In: Fifth National Climate Assessment. Crimmins, A.R., C.W. Avery, D.R. Easterling, K.E. Kunkel, B.C. Stewart, and T.K. Maycock, Eds. U.S. Global Change Research Program, Washington, DC, USA. https://doi.org/10.7930/NCA5.2023.CH30

Download citation: BibTeX     |     RIS

The Pacific Islands region is defined here as Hawaiʻi and the US-Affiliated Pacific Islands (USAPI). The USAPI comprises the Commonwealth of the Northern Mariana Islands (CNMI); the unincorporated territories of American Sāmoa, Guam, and the Pacific Remote Islands (PRI); and the Freely Associated States (FAS): the Federated States of Micronesia (FSM), the Republic of the Marshall Islands (RMI), and the Republic of Palau. The region spans a vast geography and encompasses over 2,000 islands, ranging from small low-lying atolls to large volcanic islands, with the highest peak rising to 13,803 feet (Figures 30.1, 30.2). Marine and terrestrial biodiversity and species endemism are exceptionally high. These islands (excluding FAS) total only 14,060 square miles in land area but define nearly half (47.2%) of the entire US exclusive economic zone (EEZ). The islands also support more than two dozen defense installations key to US security, including the headquarters for the US Indo-Pacific Command. As a consequence of colonization, the lands, waters, and peoples of the Pacific Islands were significantly involved in World War II,11 resulting in widespread environmental devastation, displacement of Indigenous Peoples, and nuclear weapons testing.12,13,14

The 1.9 million people who call the region home are predominantly (more than 77%) Pacific Islanders, many of whom are Indigenous Peoples (CHamoru, Chuukese, Kosraean, Marshallese, Native Hawaiian, Palauan, Pohnpeian, Samoan, Yapese, and others)—who speak more than 20 Indigenous languages15—and members of diverse communities of Asian heritage. Population is declining on all islands (except Hawaiʻi) and is increasingly urban.16,17,18,19,20,21,22 Important economic sectors include tourism, agriculture, and fishing, with government assistance, foreign direct investment, and remittances as major sources of capital. Average per capita income ranges from a high of 124% above the US average in Hawaiʻi to 4%–20% in the FAS.22,23,24 Governance arrangements across the islands vary, but all share histories of colonization that contribute to structural inequities and vulnerabilities that exacerbate the social and economic impacts of climate change (Box 30.1).14,25

Box 30.1. Historical Under-Resourcing Results in Continuing Data Inequities for the Pacific Islands Region and US Caribbean

The Pacific Islands region and the US Caribbean continue to face similar climate change–related challenges (Ch. 23; see Keener et al. 201826), including geographic isolation and reliance on imports, critical dependence on local natural resources (fresh water, fisheries), and vulnerabilities to drought, sea level rise (SLR), and natural disasters. Missing data in both regions is representative of ongoing exclusion in data collection efforts and perpetuates historical social injustices that are reinforced by colonial and postcolonial governance systems (KM 31.2). In the Pacific Islands, this has resulted in sparse and discontinuous climate data records, the absence of coastal flood hazard modeling and detailed SLR exposure mapping for most islands, a lack of downscaled future climate projections in most locations (App. 3), insufficient information about groundwater and surface water resources, and limited data on ecosystem response.15,27,28,29,30 Similar gaps are apparent in socioeconomic and health data: for example, on migration and health outcomes, including morbidity and mortality related to extreme weather events; food supply chain vulnerabilities; and resource-dependent livelihoods.31,32,33,34 Indigenous Knowledge systems and stewardship are foundational in responding to climate change, but generations of knowledge have been undervalued, suppressed, and ignored by Western science and were only recently recognized as valid knowledge sources at the federal level.35,36,37 This lack of climate-relevant data is evident throughout NCA5. Filling these data gaps could better enable data-driven decision-making and improve climate services in the region.

URL
Alternative text
Hawaiʻi and the US-Affiliated Pacific Islands
A map shows Hawai‘i and six jurisdictions in the US-Affiliated Pacific Islands. Grid lines show latitude from 10° south at bottom to 30° north at top, and longitude from 130° east at left to 150° west at right. Ocean is shown as blue, with exclusive economic zones around US islands in a paler blue. An inset map at bottom left shows the location of the main map in the context of the Pacific Ocean, Asia, and North America. Hawaii is at top right and American Samoa at bottom right. The Republic of the Marshall Islands is at center. At far left center is the Republic of Palau, and just to the right of Palau are the Federated States of Micronesia. Just above that is Guam, and just above Guam is the Commonwealth of the Northern Mariana Islands.
Hawaiʻi and the US-Affiliated Pacific Islands span a vast geography.
Figure 30.1. The map shows the geographic breadth of the state of Hawai‘i and the US-Affiliated Pacific Islands (USAPI). The USAPI comprises the US territories of American Sāmoa, Guam, and the Pacific Remote Islands (Baker Island, Howland Island, Jarvis Island, Johnston Atoll, Kingman Reef, Palmyra Atoll, and Wake Island); the Commonwealth of the Northern Mariana Islands; and the Freely Associated States: the Federated States of Micronesia, the Republic of the Marshall Islands, and the Republic of Palau. The exclusive economic zones around each jurisdiction are shown. Figure credit: University of Guam, Clark University, NOAA NCEI, and CISESS NC. Sources: Esri, Garmin, GEBCO, NOAA NGDC, and other contributors. Map image is the intellectual property of Esri and is used herein under license. Copyright © 2020 Esri and its licensors. All rights reserved.
URL
Alternative text
Detailed View of Hawaiʻi and the US-Affiliated Pacific Islands
Six maps show detailed views and topography of the islands in the Hawaii and the US-Affiliated Pacific Islands region. Clockwise from top left are Commonwealth of the Northern Mariana Islands, Hawaii, American Samoa, Federated States of Micronesia, Republic of the Marshall Islands, Republic of Palau, and Guam. Capital cities are indicated with yellow circles. Text at the bottom reads “Service Layer Credits: Esri, Garmin, GEBCO, NOAA NGDC, and other contributors.
The Pacific Islands region contains a diversity of high and low islands.
Figure 30.2. These detailed maps show the inhabited Pacific Islands region with islands and capital cities labeled. Shown are American Sāmoa; the Commonwealth of the Northern Mariana Islands; the Federated States of Micronesia (with its four states labeled: Yap, Chuuk, Pohnpei, and Kosrae); Guam; Hawai‘i; the Republic of the Marshall Islands; and the Republic of Palau. Figure credit: Clark University, Arizona State University, University of Guam, NOAA NCEI, and CISESS NC. Sources: Esri, Garmin, GEBCO, NOAA NGDC, and other contributors. Map image is the intellectual property of Esri and is used herein under license. Copyright © 2020 Esri and its licensors. All rights reserved.

Climate Variability and Change

The El Niño–Southern Oscillation (ENSO) and Pacific Decadal Oscillation (KMs 2.1, 3.3) are dominant sources of climate variability in the Pacific Islands region, affecting rainfall, air and ocean temperature, sea surface height, and trade winds (Box 27.1 in Keener et al. 201838).30,39,40,41 ENSO and other sources of climate variability interact with climate change to reduce or amplify trends and their impacts on decadal and shorter timescales. Natural variability in sea level and tides, for example, affects tidal flooding experienced at various Pacific Island locations.42,43,44

Between 1951 and 2020, annual average air temperatures across the Pacific Islands region increased 2°F (1°C).45,46 End-of-century projections indicate up to 4.5°F (2.5°C) higher temperatures at high elevations (above 9,800 feet) for an intermediate scenario (RCP4.5) and up to 9°F (5°C) under a very high scenario (RCP8.5).47 Historical precipitation trends are variable across the region, with some islands seeing long-term drying and increases in drought frequency, severity, and duration (KM 4.1).48,49,50 The magnitude and direction of projected precipitation changes are currently highly uncertain (Figure 30.3); some areas are projected to experience drying (e.g., leeward [western] areas of Hawaiʻi;51 KM 2.1), while increases in precipitation are expected for others (e.g., American Sāmoa).52

Although the findings are uncertain and geographically diverse, current analyses indicate that the frequency of tropical cyclones is expected to decrease,53 but associated wind speeds, rainfall rates, and storm surge heights are projected to increase across the entire region (KM 2.2).53,54,55,56,57

The rate of increase in regional sea surface temperatures (SSTs) has exceeded global rates, while ocean acidification (declining ocean pH)58 in the region has reached levels not seen over the past 30 years.59 These region-wide changes are projected to continue over the remainder of this century,60 with dire consequences for coral reef ecosystems (KM 10.1).61,62 Relative sea level rise (SLR) rates vary across the Pacific region,63 with the highest SLR rates observed in the western Pacific.64 With warming above 3.6°F (2°C), SLR projections of 3.5 to 7.5 feet by 2100 are increasingly possible (Figure 30.4; KM 9.1).65

URL
Alternative text
Projected Changes in Rainfall at 3°C (5.4°F) of Global Warming (Relative to 1985–2014)
Three maps at left show percent change in rainfall at a Global Warming Level of three degrees Celsius, or 5.4 degrees Fahrenheit, with the changes shown being relative to the 1985 to 2014 average. The top map shows annual change, the middle map shows November to April, and the bottom map shows May to October. The maps all show an area from 30 degrees south to 30 degrees north latitude and 100 degrees east to 80 degrees west longitude. Central America appears on the maps at far right and Southeast Asia at far left. Black outlines around Hawaii and each group of US-Affiliated Pacific Islands indicate their exclusive economic zones (abbreviated E E Z). The legend shows percent change in precipitation from negative 15 or more (dark brown) to positive 80 or more (dark green). All three maps show a band of large increases across the equator and decreases south and east of the equator. Patterns of alternating bands of decreases and increases north of the equator vary across the three maps. To the right of the maps, arrows and numbers indicate average changes in precipitation across the EEZs for Hawaii and each territory, as follows. American Samoa: annual, plus 0.4 percent; November to April, plus 1.1 percent; May to October, minus 1.2 percent. Hawaii: annual, plus 1.6 percent; November to April, minus 3 percent; May to October, plus 6.1 percent. Federated States of Micronesia: annual, plus 4 percent; November to April, plus 1.2 percent; May to October, plus 7.1 percent. Palau: annual, plus 0.8 percent; November to April, minus 1.4 percent; May to October, plus 3.3 percent. Guam and the Commonwealth of the Northern Mariana Islands: annual, plus 6.1 percent; November to April, plus 8.4 percent; May to October, plus 5.3 percent. Marshall Islands: annual, plus 4.7 percent; November to April, plus 6.7 percent; May to October, plus 4.7 percent.
Rainfall is projected to increase across most of the region with 3°C (5.4°F) of global warming.
Figure 30.3. The figure shows projected percent change in annual and seasonal rainfall by 2100 across the Pacific Islands region under a global warming level of 3°C (5.4°F) relative to 1985–2014. Large increases in future rainfall are seen for the Commonwealth of the Northern Mariana Islands (CNMI), the Federated States of Micronesia (FSM), Guam, and the Republic of the Marshall Islands (RMI), while almost no change is projected for American Sāmoa. Hawai‘i and Palau are projected to see decreases in November–April rainfall and increases in May–October rainfall. Adapted from Dhage and Widlansky 202266 [CC BY 4.0].
URL
Alternative text
Regional Sea Level Rise Projections
At the top, four maps of the Pacific show projected sea level rise in 2050 (top row of maps) and 2100 (bottom row of maps) under the Intermediate (left) and High (right) sea level rise scenarios. The legend shows sea level rise in feet as a color gradient from white to red, with values ranging from 0 (white) to 8 feet (dark red). For 2050, sea level rise is consistently about 0.75 feet across the ocean region shown for the Intermediate scenario and consistently about 1 foot for the High scenario. For 2100, sea level rise is around 3 feet for the Intermediate scenario, with some variability across areas of the Pacific. The High scenario shows much larger increases of 7 feet or more. The letters A and B on the top left map indicate the locations of Honolulu, Hawaii, (A) and Apra Harbor, Guam (B). At bottom left, a time series chart shows sea level rise from 2020 to 2100 for Honolulu for the low (blue line), intermediate-low (green line), intermediate (yellow) intermediate-high (red), and high (purple) scenarios. At 2050, sea level rise ranges between about 0.5 and 1 foot from the low scenario to the high scenario. By 2100, the range is from about 1 foot for the low scenario to more than 7 feet for the high scenario. The bottom right time series chart shows the same information for Apra Harbor in Guam. Values for 2050 again range between about 0.5 and 1 foot across the 5 scenarios. At 2100, values increase, ranging from about 0.9 feet for the low scenario to almost 7 feet for the high scenario.
Future sea levels strongly depend on the scenario, and rates will vary across the region.
Figure 30.4. Sea level rise (SLR) projections for different scenarios are as follows: Low (1 foot of global SLR by 2100), Intermediate-Low (1.5 feet), Intermediate (3 feet), Intermediate-High (5 feet), and High (6.5 feet). (top four panels) Maps display regional variations in projected SLR by 2050 (top row) and 2100 (center row) in the Pacific under Intermediate (left) and High (right) scenarios. In general, sea levels are relatively higher in the northern and western Pacific than in the southern and eastern Pacific. Although patterns vary spatially due to various processes such as thermal expansion and subsidence, the greatest sources of variability are time and the scenario. (bottom two panels) SLR scenarios are shown for 2020–2100 at Honolulu, Hawaiʻi (A), and Apra Harbor, Guam (B; locations noted in the upper-left panel). For information regarding the likelihood of these scenarios under possible future warming levels, see Appendix 3. Figure credit: US Geological Survey, University of Guam, Arizona State University, and NASA Jet Propulsion Laboratory.

Increasingly Severe Climate Impacts Are Causing Cascading Impacts for People

All Pacific Island communities are experiencing climate change impacts and, in some cases, facing existential risks (Figure 30.5). Sea level rise is compromising critical infrastructure and threatens to displace populations on low-lying atolls, forcing migration and disrupting social relationships (KMs 9.1, 9.2, 9.3). The vast majority of ports, airports, primary roads, power plants, and water treatment plants are located a few feet above sea level. Ports bring in 80%–100% of all consumer goods (including food and medical supplies) and 100% of fuel,67 placing the islands at the end of long supply chains and making them extremely susceptible to disruptions (Ch. 23). Climate change increasingly affects the lands and waters of the region crucial for sustaining primary economic and cultural livelihoods, including tourism, agriculture, fishing, forestry, and artisan practices (KMs 10.2, 18.1, 19.1, 23.2). These effects exacerbate structural inequities (KMs 20.1, 31.2).68,69 Climate change poses risks to the region’s rich biodiversity, including many threatened and endangered species, that supports functioning ecosystems and cultural practices (KMs 8.2, 16.1). Table 30.1 illustrates examples of impacts across the region for each of the chapter’s Key Messages related to water and food, human health, the built environment, ecosystems, and cultural and historical resources.

URL
Alternative text
Climate Change Indicators and Impacts in the Pacific Islands
Two similar illustrations of a stylized island landscape show climate indicators (top) and climate impacts (bottom) in the Pacific Islands. Both show at top left a “high island” with mountain peaks, a city with high-rise buildings, single-family homes, roads, waterfalls, and agricultural fields; at bottom right is an atoll with a small airport, roads, houses, and thatch-roofed huts. At bottom left is a coral reef. The indicators illustration shows the following all rising: carbon dioxide concentrations, surface air temperature, ocean heat content, sea surface temperature, and sea level. In addition, streamflow, rainfall, winds and waves, and extreme events are changing, and there are more intense and changing tropical storms. The ocean is seeing acidification and oxygen loss. In the climate impacts illustration, the high island is showing impacts to available water supply, crops and food security, and infrastructure. There are also more intense and frequent heatwaves, new diseases and risks to human health, increased wildfire risk, declines in water quality, and coastal erosion and beach loss. Coral reefs will see bleaching and loss; oceans will see shifting fisheries and biodiversity loss. Atolls will see salinization and saltwater intrusion, flooding and drainage failure, and threats to cultural practices and sites. In coral reefs and elsewhere, habitats and species distributions are changing.
Monitoring key indicators of climate change is essential for understanding impacts and informing adaptation efforts.
Figure 30.5. Changes in climate, as measured through key indicators (top panel), including sea surface temperature, sea level, and tropical cyclone intensity, result in impacts and risks (lower panel) for Pacific Island environments and communities, both on high volcanic islands and atolls. Improved monitoring of indicators is essential for tracking the pace and extent of climate change. Understanding of the connections between indicators and impacts is expanding, which supports adaptation efforts. Adapted from Keener et al. 2018,26 which was adapted from Keener et al. 2012.15

Table 30.1. Illustrative Climate Change–Related Impacts Across the Pacific Islands Region
Examples of historical, ongoing, and projected climate change impacts are given for each jurisdiction. Sea level rise is abbreviated as SLR.
Jurisdiction
KM 30.1:
Water and Food

KM 30.2:
Human Health

KM 30.3:
Built Environment

KM 30.4:
Ecosystems

KM 30.5:
Cultural and Historical Resources
American Sāmoa Increased extreme precipitation events degrade drinking water quality by stressing the water systems’ filtration capacity (KM 4.2).70,71 Hot weather worsens chronic health conditions, including heart disease and diabetes, already at emergency levels (KM 15.1).72 Climate change threatens fisheries and impacts economic infrastructure, including canneries.73 Climate change promotes invasive species spread in native rainforests, home to rare and culturally important plants.29 Coastal flooding affects villages that contain burials of relatives and ancestors.74
Commonwealth of the Northern Mariana Islands (CNMI) Access to safe drinking water is threatened as climate change exacerbates ongoing challenges of disposal of military, industrial, and municipal waste.27 Super Typhoon Yutu in 2018 negatively impacted mental health and healthcare providers.75 Two successive typhoons (2015 and 2018) damaged or destroyed significant portions of the built environment.27 Climate change aids species invasions, which threaten the high biodiversity in wetlands and forests, including endemic birds, threatened reptiles, and two species of bats.27,76 Coastal historical and cultural sites are exposed to SLR.27
Federated States of Micronesia (FSM) Warmer temperatures and saltwater intrusion are projected to increase disease in staple crops such as taro, bananas, and breadfruit.77 Changes to marine and coastal habitats threaten artisanal fisheries, a key protein source.78,79,80,81,82,83 In FSM, 59% of infrastructure (89% of population) is within 0.3 miles (0.6 km) of the coast and vulnerable to coastal climate impacts.84,85 Highly valued mangrove forests in Pohnpei will be threatened by SLR.86 Coastal men’s houses (faluw) are exposed to SLR and can benefit from historical adaptation measures.87
Guam Northern Guam Lens Aquifer is at risk from hotter weather, drought, and possible increases in demand.28,88 In 2018–2019, compound extreme events (flash flooding followed by drought and wildfire) negatively impacted human health (safety, pathogens, and respiratory issues).28 Stronger tropical cyclones around Guam will increase the potential for severe damage to the built environment.53 Increased frequency of coral bleaching89 and increased risk of wildfires are expected.28 Many cultural and historical resources located along the coast will be impacted by 3 feet of SLR.90
Hawaiʻi Increasing drought is reducing available water supplies.49 Hot weather causes heat-related illness and increases hospitalizations (KM 15.1).91 3.2 feet of SLR would cause $23.1 billion in economic loss (in 2022 dollars).92 Warming at higher elevations will expand transmission of avian malaria, causing declines in endemic bird populations.93,94 Strong winds, large storm waves, SLR, and changes in groundwater impact fishponds throughout Hawaiʻi.95,96,97
Pacific Remote Islands (PRI) Decreasing precipitation and salinization from SLR are reducing freshwater availability.98 The possibility of disappearing islands contributes to distress due to loss of identity and relationship with place (solastalgia).99 US military installations and low-lying islets are at risk from SLR, which may impact exclusive economic zones.98 The 2014–2016 El Niño bleached over 90% of monitored reefs in Palmyra Atoll.100 Sea level rise threatens remote islands and megafauna connected to the Native Hawaiian culture and creation story.101,102
Republic of the Marshall Islands (RMI) During the 2015–2016 extreme El Niño drought, the northern atolls established freshwater “filling stations” for water access.103 Sea level rise threatens health infrastructure,104 and migration harms mental health.105 Highly urbanized atolls may not be able to adapt to future SLR, leading to land loss and potential uninhabitability.98,106,107,108 Tuna catch within the exclusive economic zone is projected to decline by 10%–40% by 2050 relative to the early 2000s under a very high scenario (RCP8.5).109 Graves in the Jenrōk neighborhood on Majuro were lost to coastal erosion.110
Republic of Palau Climate change affects the timing of when crops are traditionally planted, which impacts food security.111 Mental health challenges arise from degradation of places and ecosystems essential to ocean-centered culture and livelihoods (Box 30.3; KM 15.1).112 Migration to and development in Koror's coastal zone exposes more people to SLR; king tides already flood urban areas.113 The strong 2015–2016 El Niño reduced the jellyfish population in Palau's Jellyfish Lake.113 High tides and SLR submerged and damaged Kukau el Bad, a historic healing ritual site in Ollei, Ngarchelong.113

Mitigation and Adaptation Through Indigenous Knowledge Systems, Collective Action, and Planning

Effective climate mitigation and adaptation measures for Pacific Islanders and Indigenous Peoples are grounded in local ecological knowledge, which promotes intergenerational and holistic stewardship approaches,114,115 and best available Western science (KM 18.3). Indigenous ways of knowing can revitalize resilient practices and confront environmental injustices (KMs 16.3, 31.2).14 Examples of Indigenous Knowledge–informed adaptation include agroforestry, wetland taro agriculture, fishponds, and fisheries rules such as rest periods.116,117,118,119 Mangrove and seagrass conservation and regenerative agriculture demonstrate high potential for carbon sequestration (KM 30.4).120,121,122

Collective action in the region is codified in pursuit of the Sustainable Development Goals (SDGs) through the Local2030 Islands Network and Micronesia Challenge (Box 30.2; KM 20.2). Climate literacy may help spur collective action and build social capacity to address climate-driven changes (KM 32.5). Climate change–focused education and outreach programming in the Pacific Islands region is diverse and extends across federal, state, and county levels, nongovernmental organizations, and Indigenous-serving organizations (e.g., Bolden et al. 2018; Frungillo et al. 2022; HWMO 2021; Longman et al. 2022; USGS 2021123,124,125,126,127). Native Hawaiian and Pacific Islander epistemologies are woven into many programs (KM 16.2).128,129

Box 30.2. Sustainable Development Goals and Collective Action

Many Pacific Island states have adopted the 17 United Nations Sustainable Development Goals (SDGs)130 as part of a place-based path toward climate resilience (KM 17.4). The Local2030 Islands Network is forming regional communities of practice around energy, data, tourism, and other topics of interest and is piloting SDG dashboards in Guam, Hawaiʻi, and Palau (KM 18.4). In Hawaiʻi, a scorecard provides annual progress summaries on SDGs for 2030.131 Across sectors, Hawaiʻi has progressed toward meeting 6 of 36 local SDG metrics as of 2021 and is actively measuring progress in 17 more. While strong progress was made in measuring relevant goals, additional data and efforts are needed to meet more SDGs. Hawaiʻi Green Growth and Guam Green Growth132 are diverse public–private partnerships formed to develop measurable economic, social, and environmental adaptations toward sustainability (Box 18.3). FSM’s more formal commitment to the SDGs is evident in their national Strategic Development Plan 2004–2023.133

The Micronesia Challenge is a commitment by the Commonwealth of the Northern Mariana Islands, the Federated States of Micronesia, Guam, Palau, and the Republic of the Marshall Islands to conserve at least 20% of their terrestrial resources and 30% of their nearshore marine resources. With a regional endowment fund of approximately $23.1 million (in 2022 dollars)134 providing a sustainable funding stream, the Micronesia Challenge has established over 150 protected areas throughout Micronesia, conserving biodiversity, protecting the environment, securing livelihoods and cultural practices, and enabling these islands to become more resilient to climate change.

Climate Change Impairs Access to Healthy Food and Water

Access to clean, fresh water and healthy food is expected to be increasingly impaired by climate change . On low-lying atolls, sea level rise has caused saltwater contamination of fresh water . Regionally, food and water availability will be further negatively impacted by increasing temperatures, altered rainfall patterns, increased flooding and pollution, and degradation of nearshore fisheries . Adaptation actions such as traditional farming, fishing, and land-management practices can help build more resilient water and food systems .

Changing Climate Threatens Freshwater Resources

Dependable and safe freshwater resources and associated services in tropical islands are particularly vulnerable to rising temperatures (KM 4.1), altered rainfall patterns (Figure 30.3), runoff intensity and flooding, reduced groundwater recharge, and SLR (Figure 30.4; KM 4.2). Depletion of island aquifers compounds the potential for saltwater intrusion from SLR.98,135,136 The availability of surface water for irrigation, drinking water, and hydropower is affected by increasing frequency and severity of flooding and by reductions in stream baseflow;137 water contamination through increased Staphylococcus sp., Leptospira (a waterborne pathogenic bacteria), fecal coliform bacteria, and suspended sediment (KM 15.1);138,139,140,141 and extreme drought (KM 2.2).103 In response to these changes, adaptation-focused restoration techniques are being applied, including revegetating with native species, reducing impervious surfaces, and redundant water distribution systems. Climate-induced land-cover change can have significant control over groundwater recharge, indicating that land-use adaptation is viable for managing impacts on water resources (KM 6.1).142,143 Flood frequency is projected to increase across the region,70 while drought frequency is projected to vary across the region (KMs 2.2, 4.1).27,28,29,113

Changes Undermine the Sustainability of Water Supplies

Pacific Islands potable water supplies depend heavily on accessing clean groundwater or rain catchments, while other needs, such as irrigation, are often met with surface water resources. Groundwater recharge is affected by annual or longer-scale climate processes, while surface water supplies are more sensitive to shorter-term climatic influences.144,145,146,147,148 Although few studies assess regional changes in drought, evidence is clear that Hawaiʻi has experienced a drying trend since the 1950s and in La Niña years.149,150 On atolls and low-lying islands, freshwater aquifers typically occur as very thin lenses and are highly sensitive to groundwater extraction and SLR-driven saltwater intrusion.135,136 Shifting rainfall patterns and runoff conditions are affecting the availability of surface water to meet growing demands.103 Climate change has elevated region-wide efforts to protect and conserve freshwater resources. Communities that rely heavily on rain-fed catchments and surface water are acutely susceptible to short-term and, in particular, long-term drought and the resulting reductions in streamflow.103

Salinization and Pollutants Deteriorate Water Quality

Increased intensity of extreme rainfall events, coupled with SLR, is projected to exacerbate freshwater contamination risks.151 Past and ongoing disposal of military, industrial, agricultural, and municipal waste contaminates island water supplies.35,152 Although SLR-driven mobilization of subsurface contaminants has received little study in the Pacific Islands, evidence of diverse groundwater contaminants in the region153 and their mobilization154,155 raises concerns for low-lying island aquifers (KM 4.2). Salt is a critical freshwater contaminant; wave-driven overwash135,136,156 and SLR-induced rise of the freshwater–saltwater transition zone157,158,159,160 cause salinization and saltwater intrusion.

Changes in the frequency, severity, and duration of drought, associated fires, and flooding all interact to exacerbate sediment loading to streams.103,161 Given the short ridge-to-reef distances in the region, sensitive nearshore coral ecosystems and fisheries are directly impacted by increased sediment and pollutant loads to streams,162 compromising biodiversity, subsistence practices, and economies (KM 9.2).162,163,164

Food Systems Disrupted

Climate change will increasingly impact food production, transport, processing, packaging, storage, retail, consumption, and waste for Pacific Island communities (KMs 11.2, 13.1). The aforementioned challenges will disrupt imports reliant on fragile supply chains and reduce viability of local agriculture and fisheries, thus reducing access to nutritious foods.31,165,166,167,168,169 Fisheries are the principal protein sources for many Pacific Islanders, with locally grown staple food crops such as bananas, taro, breadfruit, and sweet potato supplying critical calories and nutrients.170,171,172 However, Pacific Island communities have increasingly relied on imported foods, which come with complex and sometimes hidden environmental, financial, social, cultural, and nutritional costs (KM 30.2).173,174 COVID-19 and previous disasters exposed the fragility of global supply chains (Focus on Risks to Supply Chains) and emphasized the need to bolster local food production capacity to increase resilience.166,167,175,176

Declining Fisheries

The global capacity of coral reefs to supply fish has declined by half since the 1950s, a change that climate stressors have exacerbated (KM 9.2)62,177,178,179,180 through coral bleaching, acidification, SLR (Figure 30.4), terrestrial sediment, and contaminants (Box 30.3).78,79,181,182 Small-scale coral reef fisheries supply Pacific Island communities with a substantial portion (in some cases 50% to 90%) of their dietary protein and important micronutrients.82,172,177,183,184,185,186 Warming waters, acidification, and deoxygenation redistribute open-ocean fish stocks, and fisheries catch within regional EEZs is projected to decline by up to 40% by 2050 relative to the early 2000s under a very high scenario (RCP8.5; KM 10.1).109 Fishing fleets are ill-equipped to adapt to this deficit (KM 10.2).81,187 Warming, extreme events, acidification, and SLR may also compromise efforts to expand mariculture (marine farming), through damage to aquaculture systems,188 decreased species richness,189 and decreased local access to nearshore and open-ocean species.190,191,192

Box 30.3. Changing Fisheries: Local Knowledge from Palau

Indigenous practitioners are often the first to observe and respond to changes in the environment (KM 16.3). For hundreds of years, fishers in Palau have gathered at seagrass meadows on the sixth day after a new moon during late-afternoon low tide to catch rabbit fish using cast nets (Figure 30.6). Since 2021, fishers have been unable to participate in this age-old tradition.193 The normal low tide no longer occurs, and ocean levels remain too high for rabbit fish aggregation. It is unclear whether these changes can be attributed to SLR, human impacts (e.g., overfishing), or natural variability. If this change persists, loss of this fishery would threaten the fishers’ livelihood and resilience as ocean people (KM 10.2). Integrating place-based and complementary knowledge systems into assessments can help ensure sustainable management under future climate change.194,195

URL
Alternative text
Traditional Cast Net Fishing
A photo titled Traditional Cast Net Fishing shows two people in a small boat. The person in the back is steering the boat with a long pole while the person at the front is casting a large fishing net.
Species loss threatens the traditions, livelihoods, and resilience of Pacific Islanders.
Figure 30.6. Traditional Palauan cast net fishing remains important for local food security. Photo credit: © Reid Endress

Agriculture

Crop production in the USAPI has generally kept up with population growth over the past 20 years.165,173 Although local agriculture provides a fraction of nutritional needs in the region,165 it remains a critical food source, complementing imported foods, serving as an emergency food source, providing culturally important items, and supplementing household income and government revenue.196,197

Climate change is projected to impact island food systems through a variety of different mechanisms (KMs 11.1, 23.3).77 Warmer nighttime temperatures and saltwater intrusion, especially in FSM and RMI, are projected to increase damage from disease on staple crops such as taro, bananas, and breadfruit.77,198 Cash crops are also likely to be affected, with higher temperatures and increased plant pathogens decreasing coffee yields, increased flooding depressing sugar yields, and higher winds damaging coconut palms, bananas, and breadfruit.191 In Hawaiʻi, droughts have become longer and more severe and are the principal cause of crop loss.49

Adaptation Strategies to Improve Local Food System Resilience

Strategies are being developed and implemented across the region to revitalize healthier traditional food systems, resulting in more just access to food (KM 11.2).117,118,165,199 Subsistence-based food system practices such as agroforestry and fishing have sustained Pacific Island peoples for millennia and have aided in recoveries from natural disasters such as typhoons, earthquakes, volcanic eruptions, and tsunamis.119,171,200,201 Restoring Indigenous agroecology practices can support conservation, food security, and broader sociocultural objectives in the face of shifting precipitation and SLR (e.g., Bremer et al. 2018; Winter et al. 2020202,203). Community food-sharing networks that empowered the most overburdened to overcome economic and social hardship during the COVID-19 pandemic offer a model for resilient food systems in the face of climate change.175,204,205 Promising fisheries adaptations include establishing networks of marine protected areas to preserve coastal resources, safeguarding fish habitats from pollution runoff, and restoring traditional fishpond mariculture (KM 10.3; e.g., Bell et al. 2013; McLeod et al. 2019; Farmery et al. 202273,116,119).

Box 30.4. Food Security and Traditional Knowledge

For thousands of years, Pacific Islanders have relied on traditional food systems that now face threats from climate change. Traditional agroforestry and aquaculture investments are critical to strengthen food security and reduce reliance on food imports.4,5,206 The Melai Mai Breadfruit Project was initiated in 2016 to increase food security in typhoon-devastated outer islands of Yap, FSM.207 Importing diverse breadfruit varieties to extend the harvest length increased food production and sustainability. Other examples include programs working to identify saltwater-tolerant taro species (Figure 30.7) in Palau and distribute them to the community.111,208

URL
Alternative text
Key Agricultural Plants: Giant Swamp Taro
A photo titled Key Agricultural Plants: Giant Swamp Taro shows a crop of large-leafed green plants.
Programs aimed at supporting traditional crops help strengthen food security.
Figure 30.7. Several varieties of giant swamp taro are salt tolerant, making them valuable for adapting to saltwater intrusion. Photo credit: © Ann Singeo, Ebiil Society Inc.


Climate Change Undermines Human Health, but Community Strength Boosts Resilience

Climate change undermines the place-based foundations of human health and well-being in the Pacific Islands . Climate shocks and stressors compromise healthcare services and worsen long-standing social and economic inequities in both mental and physical health , and these negative impacts are expected to increase in the future . Adaptation efforts that build upon existing community strengths and center local and Indigenous Knowledge systems have great potential to boost resilience .

Climate change can degrade societal foundations of health and well-being, including access to shelter, nutritious food, clean water, and cultural and social relationships (KM 15.1). Prominent international frameworks and Pacific Island Indigenous conceptualizations of health and well-being recognize that the health of people is closely connected to the health of nonhuman beings, to the shared environment, and to place (Figure 16.3).209,210,211,212

Indigenous communities of the Pacific Islands have actively responded to climate-related and other health risks, as well as external economic shocks (Box 30.3; KM 16.3).119,205 However, colonization and economic disparities have resulted in disproportionately high rates of morbidity and mortality for Native Hawaiian and Indigenous Pacific Island peoples (KM 15.2).213 Moreover, Pacific Island populations experienced severe economic shocks during the COVID-19 pandemic (KM 30.3),214 which interacted with existing societal and non-climate stressors that worsen health inequities (KM 18.2).

The Health Impacts of Extreme Events

Tropical cyclone intensity,53,215,216 drought frequency,150,217 and flood potential (KMs 30.3, 2.2)70,98,218,219 are expected to increase and continue to aggravate social and geographic inequities (KMs 2.2, 4.2, 10.1, 16.1, 17.4).53,98 Extreme weather impacts health in ways that persist beyond the initial disaster,220,221 including increases in food- and waterborne pathogens, loss of access to medications and emergency services, loss of electricity needed for medical equipment and medical facilities, and disruptions to transportation networks, all of which increase illnesses and deaths (KM 15.1).222 Healthcare facilities in the Pacific Islands are located primarily on coastlines, making them especially susceptible to tropical cyclones and SLR-driven flooding (KM 9.2),104,223 with limited space and resources for relocation (KM 30.3).

The built environment is especially affected by extreme weather because of high costs of building materials, supply shortages, delays in code updates, and physical isolation (Figure 30.8; KM 30.3).224 Given the limited emergency infrastructure and evacuation options, extreme weather events create high risks for the mental and physical health of island populations, with individuals with low-income, older adults, children, and persons with disabilities at disproportionately higher risk (Box 15.1).26,225,226,227

Drought poses health challenges, particularly for rural island populations. A 2013 drought in the northern atolls of RMI caused crop failures and unsafe and insufficient water supplies, which led to nutritional deficits and increased prevalence of infectious diseases, especially in children.103,228 Severe wildfires, which occur primarily during droughts,229,230,231 directly threaten health and safety and can create respiratory hazards (KM 14.2).232

URL
Alternative text
Damage from Typhoon Yutu
A collage of three photos titled Damage from Typhoon Yutu. At top left, three people in military clothing are working to shift debris in front of a damaged structure. At top right, a NOAA satellite infrared image shows Super Typhoon Yutu on October 24, 2018. The location of the island of Tinian is shown in the center, surrounded by the eye of a very strong tropical cyclone. At bottom: A photo of the interior of a classroom shows extensive damage, with much of the roof having caved in.
Extreme events acutely affect Pacific Island communities and their built environment.
Figure 30.8. In 2018 Super Typhoon Yutu struck the Commonwealth of the Northern Mariana Islands and damaged or destroyed a significant portion of the islands’ buildings and critical infrastructure, leaving a sizable population temporarily unhoused. The experience underscored how events such as cyclones, flooding, and droughts combine with societal factors to acutely affect human health and safety. Images show US Naval personnel clearing debris at a Tinian family’s home destroyed by Super Typhoon Yutu (top left); a satellite infrared image of Super Typhoon Yutu (top right); and a classroom in Hopwood Middle School on Saipan after the storm (bottom). Image credits: (top left) Matthew R. White, US Navy; (top right) NOAA/UWM-CIMSS, William Straka III; (bottom) Grace Simoneau, FEMA.

Health-Associated Impacts from Migration

Under a very high scenario (RCP8.5), human migration will increase due to SLR-driven inundation and salinization, displacing people, even entire populations, from low-lying atolls and low-elevation areas of high islands, with enormous implications for health and well-being (KMs 15.1, 17.1, 20.3).98,105 Migrants often have difficulty navigating foreign healthcare systems233 and face other barriers to accessing healthcare, including ineligibility for federal programs.234 An improved understanding of the experiences and health outcomes of people who migrate, within or away from the USAPI, could inform better policy.

Mental Health Consequences and Climate Grief

Climate change directly and indirectly affects the mental health of Pacific Islanders.235,236,237 On some islands globally, local climate stressors (such as floods, droughts, and SLR) are linked with negative mental health outcomes such as sadness, distress, and anger (KM 15.1).238,239,240 Across the Pacific region, studies show that rural populations, socioeconomically disadvantaged groups, and people with disabilities experience more severe mental health consequences from various climate impacts (KM 15.2).105,239,240,241,242

Research is limited on the mental health impacts of climate-induced migration. Instability caused by voluntary and involuntary migration is expected to be a continuing source of anxiety,99 although evidence indicates that social cohesion and reducing disparities can counter negative impacts.105,243 Some data show that distress from thinking about climate stressors can be comparable to that from experiencing direct impacts.239 Additionally, because Indigenous People in the Pacific are strongly connected to place, and place is central to conceptions of cultural identity, sudden ecological devastation or gradual change to the environment can create considerable stress (KMs 10.1, 15.1, 15.2, 23.1, 29.1).99

Mental health services related to climate change show effectiveness when they are designed to serve Pacific Islander populations in a culturally centered way and include diverse ways of knowing.235,243,244 Finally, the lack of studies on mental health and climate change in Hawaiʻi and the USAPI indicates that additional research may provide a more nuanced understanding of local implications. 

Increase in Vector-Borne Disease

Outbreaks of mosquito-borne diseases such as dengue, chikungunya, and Zika are increasing in frequency, extent, and duration across the region.245,246 Changes in rainfall (Figure 30.3) and temperature, combined with environmental and demographic changes, are anticipated to exacerbate this trend.34,247 Resources for vector control and managing outbreaks are limited on small tropical islands, and outbreaks sometimes overwhelm health systems.245,247 Health officials in FSM, RMI, and Palau are developing predictive modeling to create a dengue early warning system.248 Similar to how chikungunya and Zika recently emerged and expanded in the Pacific, other vector-borne diseases may emerge in the future.249

High Temperatures and Heat-Related Illness and Death

As in much of the US (Figure 2.11), the number of hot days has increased across the Pacific Islands; 2020 was the region’s hottest year on record.27,28,29,45,113 A community heat assessment in Oʻahu, Hawaiʻi, in August 2019 found many neighborhoods with record-high afternoon heat indices between 100°F (38°C) and 107°F (42°C) (Figure 30.9).250,251

Climate change–driven hot weather causes heat-related illness and increases hospitalizations and deaths; 82% of heat-related deaths in Honolulu are already attributable to climate change (KM 15.1).252 Those more likely to experience heat-related illness include young children, older adults, outdoor workers, economically burdened and disadvantaged people with little access to cooling or healthcare (KM 15.1), military personnel whose duties require heavy gear and vigorous activity, and non-acclimated visitors.91 Shock events interact with heat: for example, after the 2009 tsunami in American Sāmoa, dehydration, heat stress illnesses, and barriers to receiving medical care increased.253

Imported low-quality foods have replaced local, nutritious, traditional diets (KM 30.1), resulting in some of world’s highest prevalence of noncommunicable diseases (NCDs).165,190,199,254,255 Heat worsens health outcomes for people with NCDs such as heart disease, cancer, stroke, and diabetes256 and creates challenges for the management of obesity and other diseases because exercise is more difficult to do safely. Overweight and obesity in young children are at a higher prevalence in American Sāmoa, CNMI, and Guam than globally.257

URL
Alternative text
Oʻahu Community Heat Assessment (August 31, 2019)
Two topographical maps show a community heat assessment for O‘ahu for August 31, 2019. The main map shows the island of O‘ahu and identifies cities and other locations around the island. Shades of yellow and red indicate the afternoon heat index in degrees Fahrenheit, according to a legend with values ranging from 90 or less (light yellow) to 102 or more (dark red). Heat index values are generally higher at the lowest elevations along the coast, with values generally somewhat cooler inland and upslope. Many of the coastal areas show values of 98 to 100 or 100 to 102, and a few areas of 102 or more. An inset map at top right shows a close-up view of Honolulu and Waikīkī, with roads, Pearl Harbor, Daniel K. Inouye International Airport, and Waikīkī labeled.This map shows significant localized variability, with temperatures of around 92 to 94 near the airport to values of 100 or more in many other areas, particularly where roadways suggest more developed land.
High temperatures are responsible for heat-related illnesses, hospitalizations, and death.
Figure 30.9. This community heat assessment map shows the afternoon heat index and “hotspots” for the island of Oʻahu, Hawaiʻi. The inset is urban Honolulu. Data were collected by community volunteers and the City and County of Honolulu on August 31, 2019. On this day, the high temperature tied the hottest-ever recorded for Honolulu. Multiple neighborhoods on Oʻahu experienced afternoon heat indices above 100°F (38°C), with a maximum recorded heat index of 107.3°F (42°C). Climate change is increasing the frequency, intensity, and duration of heat extremes, putting individuals and communities at risk. Figure credit: Arizona State University, University of Hawaiʻi at Mānoa, NOAA NCEI, and CISESS NC.

Social Adaptive Capacity and Community Resilience

The ability of individuals, communities, and institutions to endure stress and adapt to change determines health impacts of climate change. Recent examples demonstrating the importance of social capital (such as community networks, equitable access to education [KM 15.3], sharing, and relationships) in disaster response include community initiatives addressing flooding on the island of Kauaʻi258 and drought in RMI.259 Traditional Knowledge and coping strategies can enhance adaptive capacity and disaster response in some contexts.260,261,262,263 The resilience of organizations, including health-related institutions and disaster response systems, depends on the ability of organizations to form relationships and communicate with one another, participation by traditional leaders and faith organizations, and effective planning by disaster management agencies (KMs 16.2, 20.2).227,264,265,266,267 Prioritizing social and mental health initiatives in the health sector would aid in responding to the psychological issues that emerge with disasters and climate change.268


Rising Sea Levels Threaten Infrastructure and Local Economies and Exacerbate Existing Inequities

Climate change, particularly sea level rise (SLR), will continue to negatively impact the built environment and will harm numerous sectors of the islands’ economies . SLR intensifies loss of territory and exclusive economic zones, particularly in low islands . Climate-driven changes will exacerbate existing social challenges by disrupting livelihoods . Adaptation to climate change and recovery from disasters is logistically challenging and disproportionately more expensive in the islands . Government and community groups have developed innovative ways to reduce emissions and improve resilience by moving toward renewable energy and green infrastructure, nature-based urban planning, forward-looking building codes, and sustainable and equitable economic growth, guided by Western science and Traditional Knowledge.

Built Environment

The built environment refers to all human-made structures, including buildings, transportation infrastructure (ports, airports, roads, and bridges), military installations, and distribution systems for food, water, wastewater, communications, and power (electrical, oil, and gas). For this region, it includes traditional structures such as burial grounds, fishponds, and taro terraces (KM 30.5). These structures are critical to connecting people and providing access to goods and services, yet their location within a few feet of sea level renders them particularly vulnerable to SLR (Figure 30.4) and natural disasters (KM 9.2). For example, 98% of RMI’s and 80% of Palau’s built infrastructure is located within approximately 1,600 feet of their coastlines.85

Impacts to Infrastructure

Sea level rise will increasingly impact coastal infrastructure through increased magnitude and duration of storm wave–induced flooding (KMs 2.2, 9.1),98,219,269 rising high tides,270 and increased coastal erosion (Figure 30.10).271 In Hawaiʻi, 3.2 feet of SLR above 2000 levels, which could occur as soon as 2100 under the Intermediate SLR scenario or 2070 under the High scenario (for information on the likelihood of these scenarios, see Appendix 3; Figure 30.4),65 would affect 550 cultural sites, 38 miles (6%) of major coastal roads, 6,500 structures, and 25,800 acres of land, potentially displacing 20,000 residents and incurring $23.1 billion (in 2022 dollars) in economic loss.92 Approximately 3 feet of SLR is projected to affect at least 58% of Guam’s built environment90 and most atolls in FSM and RMI.98 Highly urbanized atolls may not be able to adapt to future SLR (KMs 9.2, 12.2),106,107 leading to land loss and potential uninhabitability.98,108 Elevated SSTs can increase bleaching and degradation of coral reefs, which are some islands’ primary natural defenses (Figure 30.11; KM 30.4) against coastal flooding.272 Lastly, increased flooding and erosion due to SLR and stronger future cyclones threaten US military bases in the region, potentially destabilizing regional security and the ability of the Department of Defense to respond to natural disasters (KM 17.1).53

URL
Alternative text
Coastal Flooding Events
A collage of four photos titled coastal flooding events. Top left: a truck is driving through waters up to its wheels, and multiple cars with water up to bumper level are visible in the background. Top right: water levels rise close to the level of a building. Water flows under a park bench that sits on a concrete structure. Bottom left: several houses are shown sitting above a beachfront area, and one of the houses has partially collapsed onto the beach below. Other debris and erosion is visible at left. Bottom right: A house is visible at right, with waterlogged ground in front of it. Several palm trees sit in this inundated land, and mountains are visible in the background.
Sea level rise is increasingly impacting infrastructure and communities.
Figure 30.10. Rising sea levels are increasing the frequency and magnitude of coastal flooding events. (top left) Cars travel through king tide flooding on Oʻahu, Hawaiʻi, in August 2019. (top right) High tide inundates a low-lying coastal area in Majuro, Marshall Islands, in February 2020. (bottom left) A residence on Oʻahu, Hawaiʻi, has collapsed due to coastal erosion during a large wave event in February 2022. (bottom right) American Sāmoa experienced flooding around homes in May 2021. Photo credits: (top left) Maya Walton via © Hawaiʻi Sea Grant King Tides Project, 2019 [CC BY 4.0]; (top right) Max Sudnovsky via © Hawaiʻi Sea Grant King Tides Project, 2020 [CC BY 4.0]; (bottom left) © Shellie Habel; (bottom right) Kelley Anderson Tagarino via © Hawaiʻi Sea Grant King Tides Project, 2021 [CC BY 4.0].
Art × Climate
Black and white photograph shows a person with lighter skin standing on a sandy beach looking toward houses along the coastline that are perched at the edge of a sand berm. One house has collapsed into the sand below.

J. Matt
Structure Failure on O‘ahu in the Global Warming Era
(2022, photography)

Artist’s statement: The Ke Nui structure failure illustrates the complexity of coastal climate politics. The owners are native Hawaiians who have kept the building in the family for five generations — descendants of a thriving kingdom overthrown under threat of U.S. arms. Receding coastlines will force reckoning with not only issues of historical Indigenous exploitations and wealth concentration but also community, individual, and states’ rights pertaining to physically indefensible coastal private property. Without a coastal action plan, property owners in Hawai‘i rely on illegal courses of action when responding to catastrophes such as this one.

View the full Art × Climate gallery.

Artworks and artists’ statements are not official Assessment products.

Adapting the Built Environment

Protecting coastal infrastructure on small islands is costly and requires strong governance and thoughtful urban planning.273 Hawaiʻi has enacted forward-looking state and county policies, including increased minimum setbacks for coastal development,274,275,276 setbacks incorporating science-based erosion rates and long-planning horizons that account for future SLR,275,277,278,279 a first-in-the-Nation mandate to disclose SLR hazards prior to real estate transactions,280 a requirement for state agencies to assess and plan for SLR impacts,281 and a mandate that environmental impact assessments consider SLR and other climate factors.282 While evaluating a balance between public and private property interests (KM 30.5), Hawaiʻi is also assessing the feasibility of relocating some coastal developments,283 prohibiting most coastal hardening,274 and helping to preserve public beach access.283

Nature-based solutions such as coral reef restoration284,285 have been proposed at the federal (DARPA Reefense Program),286 state (e.g., State of Hawaiʻi 2021287), and territorial288 levels. Such solutions are potentially cost effective for protecting coastal infrastructure289 and habitats, sustaining ecosystem services such as fisheries (KM 30.1), and supporting tourism and recreation.290

URL
Alternative text
Annual Risk Reduction Benefits Provided by Coral Reefs
Two four-panel maps showing (clockwise from top right) Hawaiʻi, American Sāmoa, Guam, and Saipan and Tinian illustrate the annual risk reduction benefits provided by coral reefs. The maps at left, labeled potential population at risk, have a legend showing people per mile, ranging from 3 or fewer (white) to 700 or more (dark red). Gray indicates areas with zero population at risk. Almost all interiors of the islands are gray, but many coastal areas show population at risk. In Hawai‘i, O‘ahu shows by far the largest population at risk, with coastlines in the area of Honolulu and other highly developed areas showing populations of 100 to 700 per mile. Kaua’i, Maui, and the Big Island show mostly 0 to 3 people per mile, with small areas of 10 to 300 people per mile near cities. Hawaii’s other islands show 0 to 3 people per mile. Guam shows mostly 0 to 3 people, with small stretches of 3 to 30. In the Northern Mariana Islands, Saipan shows mostly 0 to 3, with small stretches of up to 100 people, while Tinian is entirely 0 to 3. In American Samoa, Tutuila shows a number of stretches of 10 to 100 people, while Ofu-Olosega and Ta’u show 0 to 3. The maps at right, labeled damages and economic interruption, have a legend showing millions of dollars per mile from 0 (gray) to 0.5 or less (pale orange) to 50 or more (dark red). Patterns on the maps align closely with population figures, with higher population correlating with larger economic damages. More densely populated areas of Hawaii show potential losses of up to $50 million per mile, while those in Guam, the Northern Mariana Islands, and American Samoa show losses of up to $25 million per mile. The large stretches of coast with little or no population show losses of less than $0.5 million per mile.
Coral reef degradation could affect thousands of people and cause millions of dollars in damages.
Figure 30.11. The maps show coastal flood protection that the top-most 3.28 feet (1 m) of coral reefs provide annually in American Sāmoa; Guam; Saipan and Tinian (Commonwealth of the Northern Mariana Islands); and Hawaiʻi. The maps display (a) the number of people per mile at risk and (b) the potential economic losses (in millions of dollars per mile) from direct building damages and indirect economic disruption from flooding. Adapted from Storlazzi et al. 2019.291

Livelihoods and Economy

Demographics and Migration

Compared to Hawaiʻi, the USAPI have smaller populations and smaller land masses, as well as fewer financial resources, making adaptation more challenging. During 2010–2020, populations increased in Hawaiʻi and decreased in American Sāmoa, CNMI, Guam, and Palau.16,17,18,19,20,21 Pacific Islanders are moving from rural to more urban areas that sometimes lack resources and infrastructure to accommodate influxes of people.273,292 Migration is a traditional strategy for coping with resource scarcity in Micronesia—for example, a family member often migrates to an urban area for employment, sending money home to support family needs.293 In 2020, these external remittances accounted for 5.7% of FSM’s GDP, 0.08% of Palau’s GDP, and 12.7% of RMI’s GDP.294,295,296 As livelihoods in climate-sensitive sectors are impacted by climate change, the amount of money migrants send to relatives will be affected. Climate change may displace populations,297 but the extent to which climate change drives migration is not well established because migration is an inherent part of Pacific Island cultures.298 However, some evidence points to a strong correlation between climate impacts on ecosystem services (e.g., food and water provision, protection against floods and storms) and people’s propensity to migrate.299

Economy

The costs of adapting to, mitigating, and suffering the consequences of climate change are projected to increase over time, amounting to between 3% and 13% (under the 450ppm and SRES [Special Report on Emission Scenarios] A1FI scenarios, respectively) of Pacific Island regional GDP by 2100 (KM 19.1).300 Relative to Hawaiʻi and larger countries, USAPI economies have smaller total GDPs and GDP-per-capita and higher dependence on fisheries and agriculture—climate-sensitive industries representing a large portion of GDP.301 They also are more dependent on remittances, federal aid, and foreign aid (KM 17.1).302,303

Tourism is a major economic engine in the Pacific.304 Before COVID-19, tourism accounted for over 80% of total exports for Palau and less than 20% for RMI305 and approximately 25% of total GDP in Hawaiʻi. Climate change impacts tourism-based jobs and revenue. Damages to the built environment, especially coastal infrastructure, deterioration of natural assets, and expanding vector-borne disease occurrence could reduce tourism.300

Fishing is a critical economic sector in many Pacific Islands.178,306 Tuna license revenues represent a significant source of government income for the FAS but are expected to decline due to projected changes in fish availability in the EEZs (KMs 10.1, 10.2),79,80,81,83,306 with ramifications for local canneries in American Sāmoa and the FAS. Changing coastlines and potential land loss from SLR may result in changed maritime entitlements via changes in the size and shape of the respective EEZs,306 affecting not just fisheries but also marine mineral rights. Climate-related marine and coastal habitat impacts threaten artisanal fisheries, a critical source of food and income for many households (KMs 30.1, 10.1, 10.2).78,82,178,184

Estimated Economic Costs of Climate Change

The estimated economic impacts of climate change will vary by sector. Coastal hazards have a disproportionately large impact on small islands’ GDPs.307 Specifically, the projected increased duration and magnitude of storm wave–induced flooding98,219,269 and increased coastal erosion271 can damage infrastructure underpinning the local economy. Degradation of coral reefs due to a rise in SSTs272 could incur coastal damages costing approximately $1.2 billion (in 2022 dollars) annually to the economies of Hawaiʻi and the US Pacific territories.218

In American Sāmoa and Guam, coastal flooding and erosion are projected to disproportionately harm at-risk individuals, including minority and low-income populations and those younger than 16 or older than 65 (groups defined by the 2010 US Census data).218 High-risk coastal properties (i.e., those located in hazard-erosion areas of updated FEMA Flood Insurance Rate Maps) will be difficult to insure.308 Increased coastal flooding events and drought are expected to negatively impact agricultural revenues (KM 30.1). For example, between 2008 and 2016, Hawai‘i lost approximately $53.5 million (in 2022 dollars) in cattle production due to the most severe drought on record, and federal crop insurance programs paid $11.2 million (in 2022 dollars) to farmers for drought losses during 1996–2018, mainly for macadamia nuts and coffee.49

Adapting Livelihoods and Economies

As a percentage of GDP, the costs of climate change adaptation are significantly higher for small islands than for larger countries.300,309 Islands’ geographic isolation, reliance on imported goods, and vulnerable infrastructure can increase adaptation and disaster recovery costs (see Figure 30.8).224 Hawaiʻi and the USAPI have adopted the United Nations Sustainable Development Goals (Box 30.2)130 to increase resilience by creating more equitable approaches to adaptation and mitigation. Financing costly climate adaptation is a shared international challenge for the FAS (KM 17.4).300,301 Unlike American Sāmoa, CNMI, Guam, and Hawaiʻi, the sovereign FAS are eligible for foreign direct investment and receive substantial funding from the Green Climate Fund,310 the Asian Development Bank,311,312 the US Government via the Compact of Free Association,310,313 and other nations (KMs 19.2, 19.3).314 Because credit agencies are increasingly considering vulnerability to climate change as a factor in their ratings, however, Palau’s and RMI’s credit ratings may decrease, with negative impacts on their abilities to borrow external funds, attract foreign investment, or access below-market-rate financing to accelerate development.315

Decarbonization, Sequestration, and Resilience

Although many Pacific Islands emit minimal greenhouse gases, they are striving to reduce emissions and sequester carbon while addressing ecosystem resilience needs.119 For example, Guam and Hawaiʻi established 100% renewable portfolio standards for the electricity sector, to be achieved by no later than 2045.316,317 Hawaiʻi established a net-negative emissions target by 2045 and created a sequestration task force282 charged with establishing baselines and benchmarks, recommending policies including mitigation, and developing strategies for sustainable agriculture. This work led to a carbon pricing evaluation.318 Similarly, RMI pledged emissions reductions of 45% below 2010 levels by 2030 and carbon neutrality by 2050.319 Palau recently committed to 100% energy generation from renewable sources by 2032.320 Opportunities exist for ecosystem-based, place-based adaptation and mitigation informed by Indigenous Knowledge systems (KMs 30.1, 30.5).321,322,323

With limited land areas, each island in the region is carefully evaluating options for transitioning to renewable energy. In 2016, American Sāmoa’s island of Taʻū transitioned its energy supply from 100% diesel to 100% solar with battery backup.324 In Hawaiʻi, rapid growth of rooftop solar generation—combined with centralized solar, battery storage, wind power, and pumped hydropower storage—is enabling a transition away from an oil-predominant grid.325 The potential for success is high: Kauaʻi’s grid achieved a 69.5% renewable portfolio standard in 2021, and the island is occasionally 100% renewably powered during midday hours; it is projected to achieve a 90% renewable portfolio by 2026.326,327 Hawaiʻi’s Act 100328 required a community-based renewable energy program; power utilities and communities in the region are now developing mechanisms to enable shared ownership of renewable infrastructure.329


Responses to Rising Threats May Help Safeguard Tropical Ecosystems and Biodiversity

The structure and composition of Pacific Island coastal and marine ecological communities are directly threatened by rising ocean temperatures, ocean acidification, and sea level rise . Increasingly severe droughts and warming are increasing fire risk and will have broad negative impacts on native plants and wildlife, including an increased risk of forest bird extinctions . Adaptation strategies improve the resilience of ecosystems, including ecosystem protection, ecological restoration, invasive species prevention and control, and investments in fire prevention .

Marine and Coastal Ecosystems

Pacific Island marine environments serve as the foundation for local food systems and cultures (Figure 30.12). Rising ocean temperatures, declining dissolved oxygen concentrations, and marine heatwaves are projected to impact the structure and composition of marine ecosystems (Figure 30.5; Ch. 8; KM 10.1).330 Global marine food web models project biomass declines of 10% to 40% across the region throughout this century, with greater declines projected for large predators.331 Finally, marine species within the region’s EEZs are projected to shift beyond historical ranges as early as 2030—sooner than much of the globe.83

FOCUS ON

Blue Carbon

Blue carbon refers to carbon captured by marine and coastal ecosystems, such as mangroves, coastal wetlands, and seagrasses. Coastal ecosystems sequester carbon at a much faster rate than terrestrial ecosystems, and the carbon stored belowground can remain in place for decades to millennia if undisturbed by humans or extreme events.

Read More

Coastal and oceanic environments supply direct goods and services such as fish, recreation and tourism areas, regulating services such as coastal protection and carbon storage, and means for trade and transportation—collectively valued at over $3.1 trillion per year (in 2022 dollars; KM 23.2).332 Rising SSTs and marine heatwaves continue to be the most pressing climate change impacts facing Pacific reefs,333,334 leading to more frequent and severe bleaching events with less recovery time.61,62,335,336 Bleaching-induced mortality has reduced coral cover and decreased available habitat for reef-associated species.62,334 Increased SSTs will negatively affect some animal species distributions,337,338,339 and rising ocean and sand temperatures lead to a higher ratio of female sea turtles observed around the Pacific, threatening the viability of sea turtle populations.340 Increased air temperatures and reduced precipitation are likely to have negative effects on coastal vegetation341 and coastal pond communities,342 adversely affecting coral reefs, seagrasses, and mangroves via altered sediment and pollutant delivery to coasts.343 Increased ocean acidity344 and increased nutrient runoff from the land345 negatively impact corals, shellfish, and associated fisheries (KM 30.1). Although these systems generally have limited capacity to adapt to large climatic changes, regional strategies are being developed to reduce impacts.337,338,346

Art × Climate
Yarn is woven into round flower- or coral-like shapes in shades of (from top left to bottom right) purple, blue, orange, green, yellow, and white, against a black background.

Constance Collins
Coral Conundrum: Dead or Alive
(2023, handmade paper, upcycled warp yarn remnants)

Artist’s statement: Coral reefs are being threatened globally from climate change, unsustainable fishing, and land-based pollution. This piece recalls coral reefs and their inhabitants. As reefs deteriorate, they lose their vibrant color and their ability to provide nutrients and shelter to thousands of marine species. Here, the gradation from color to monochrome represents the bleaching that occurs as coral dies. We need to protect these crucial ecosystems, or we lose them. I used upcycled remnant warp yarns for the coral clusters and created handmade paper.

View the full Art × Climate gallery.

Artworks and artists’ statements are not official Assessment products.

Box 30.5. Blue Carbon Ecosystems

USAPI mangroves and seagrasses are among the world’s most productive blue carbon ecosystems (BCEs—ocean and coastal ecosystems that capture carbon; see Focus on Blue Carbon),347 storing over 30% of total island carbon despite their small area.120 Guam, the Republic of the Marshall Islands, the Federated States of Micronesia, and Palau plan to use BCE carbon to offset emissions while also protecting coastal infrastructure.285,348,349 BCEs also provide food, fiber, fuel, and income to Pacific Islanders.350 Mangroves are non-native to Hawaiʻi and threaten shorebird habitat, coastal access, and cultural sites and services.351 However, evidence suggests that these non-native species can provide some ecosystem benefits, for example, by significantly increasing coastal sediment accumulation352 and carbon capture rates.353 Mangrove loss in Micronesia is projected to start by 2080 under Intermediate SLR scenarios (Figure 30.4).86 The conservation and restoration of BCEs and their associated reef systems provide cost-effective solutions for protecting coastal communities and increasing other benefits (KM 8.3).289

Sea level rise will cause more frequent and extensive flooding of coastal ecosystems, impacting plants354,355 and animals,356 especially on low-lying atolls such as those in the Northwestern Hawaiian Islands, PRI, RMI, and FSM. In some cases, flooding is likely to increase erosion rates, reducing the elevation of mangroves, vegetated dunes, and beaches. Development exacerbates these drivers by exposing soils, creating impervious surfaces, and impeding inland migration of coastal ecosystems, limiting their adaptive capacity.357

URL
Alternative text
Characteristic Ecosystems of the Pacific Islands
Six photos are shown. Top left: a shoreline mangrove forest at low tide, with one person standing at center and two people sitting in kayaks near the roots. Top center: a green succulent plant in foreground against a background of bare brown hills. Top right: a large brownish coral against a background of blue water. Bottom left: white cliffs, topped by a green forest, rise over a body of water. Bottom center: a tree with green leaves grows in an area where lava rock is visible on the ground. Bottom right: a person with a backpack and wearing rain gear walks on a narrow trail in a lush vegetated area.
Pacific Island marine environments provide the foundation for local food systems and cultures.
Figure 30.12. Pacific Islands offer a diversity of ecosystems that include mangroves (top left), limestone forests (bottom left), tropical alpine habitats (top center), dry forests (bottom center), coral reefs (top right), and cloud forests (bottom right). Photo credits: (top left) Richard Mackenzie, USDA Forest Service; (top center) © Paul Krushelnycky, University of Hawaiʻi; (top right) © Underwater Earth / XL Catlin Seaview Survey / Christophe Bailhache; (bottom left) Christian Giardina, USDA Forest Service; (bottom center) Hawaiʻi Department of Land and Natural Resources; (bottom right) Lucas Fortini, USGS.

High Island Ecosystems

Terrestrial ecosystems of high islands (i.e., islands characterized by volcanic origin and consequently more diverse topography) have evolved in isolation from continental areas, resulting in unique and diverse fauna and flora with a high proportion of native species naturally occurring only on these islands (Figure 30.12). However, the combination of invasive plants and animals and diseases; habitat destruction; and intensifying fire regimes and ecological drought has resulted in severe range contractions and native species extinctions.93,358,359,360,361,362,363

In Hawaiʻi, past droughts and rainfall variability had landscape-level impacts on vegetation364,365 and cascading ecological effects.366 Long-term climatic shifts are likely to accelerate range contraction and extinction rates,93,367 but responses will vary by species, including differences in drought tolerance across populations.368,369,370,371

Rainfall changes (Figure 30.3) will affect island aquatic ecosystems. In Hawaiʻi, declines in dry-season streamflow will result in more intermittent streams137 and loss of habitat connectivity and conservation value.372 Decreased streamflow will also negatively impact stream organisms by reducing fitness and increasing disease and habitat for invasive fish and mosquitoes.373,374,375

Across the region, climatic shifts are expected to impact native ecosystems via interactions with fire (e.g., Trauernicht 2019; Nugent et al. 2020376,377). Wildland fires already burn a higher proportion of total land area in the Pacific Islands than in the continental US (Figure 30.13)229,378 and are strongly linked to El Niño events.49,103 While limited future climate projections indicate increasing fire probabilities,377 the future of fire in the region is highly sensitive to management and policy decisions, since ignitions are largely caused by humans (e.g., Dendy et al. 2022; Trauernicht et al. 2015229,378). Education and outreach will continue to play a critical role in wildfire mitigation (e.g., HWMO 2021125).

URL
Alternative text
Wildfire Area Burned in the Pacific Islands Compared to the Western US
A horizontal box plot shows wildfire area burned in the Pacific Islands compared to the western US. A box at top right provides a key to the box plots, noting that the horizontal boxes indicate the 25th to 75th percentile range, thick vertical lines indicate the median value, and horizontal whiskers indicate the minimum and maximum values. Dots indicate the individual annual observations. The x axis shows percent of land burned annual and ranges from 0 to 9. Values shown are as follows: 1) western US, 2002 to 2021,the 25th to 75th percentile range shown by the box is about 0.5 to 1 percent. 2) Hawai‘i, 2002 to 2021, box values range from about 0.25 to 0.75 percent. 3) Palau, 2012 to 2021, box values range from about 0.5 to 0.9 percent. 4) Saipan, 2016 to 2021, box values range from about 0.75 to about 1.5. 5) Tinian, 2016 to 2021, box values range from about 1.25 to 2.5 percent. 6) Rota, 2016 to 2021, box values range from about 0.7 to more than 4.5 percent. 7) Guam, 2002 to 2021, box values range from about 3 to more than 5 percent. 8) Yap, 2012 to 2021, box values range from just above 0 to about 1.1 percent. Several islands show outlier years with larger values, including years with more than 7 percent burned for Rota, Guam, and Yap.
Wildfires burn large percentages of land in Pacific Islands compared to the western US.
Figure 30.13. The annual percentage of total land area burned for seven Pacific Islands is equivalent to or greater than the percent area burned for western US states. Years examined are noted for each location. Figure credit: USDA Forest Service, USGS, NOAA NCEI, and CISESS NC.

Interactions between invasive species and climate change in isolated Pacific Islands are complex (KM 8.2),379,380,381,382,383 with climate change most often exacerbating invasion.384,385,386,387 Invasive species may aggravate local water stress, for instance, by using more water resources than native plants148,380,388,389 or by causing less rainfall to reach the forest floor, as in the case of strawberry guava invasion.148,390 Similarly, fire-prone invasive vegetation is likely to further increase future climate-driven fire risk.377 With the steep increase in the number of naturalized species on Pacific Islands,391 these climate and invasion interactions will become increasingly important for managers to address.392 Critical region-wide investments are being made to prevent the introduction of potentially invasive species and diseases,393 given that climate change can alter pathways for species introductions.394,395,396

Responding to Rising Threats

Regional efforts increasingly focus on restoration management that enhances climate resilience.397,398,399,400,401 Besides boosting adaptive capacity,402 ecosystem restoration efforts may provide multiple benefits to islands, including hydrological (KM 8.3)140,148,161,401,403,404 and sociocultural benefits,404,405 as well as carbon sequestration406 and sediment retention.407 Hawaiʻi and the USAPI have established both marine and terrestrial protected areas (Box 30.2),119,134,408,409 which elsewhere have successfully supported ecosystem resilience under climate change (e.g., Gaüzère et al. 2016; Lawler and Hepinstall-Cymerman 2010; Roberts et al 2017; Virkkala et al. 2014410,411,412,413).

The urgency of conservation actions (Figure 30.14) is exemplified by the Hawaiian forest bird crisis. Forest bird populations are declining due to avian malaria spread driven by warming.414,415 Managers are exploring options for safeguarding species near extinction,416,417,418,419 including habitat restoration, avian malaria vector control,420 and translocation.421,422,423,424

In addressing these myriad challenges, conservation efforts increasingly involve broader partnerships with educators (e.g., Bolden et al. 2018123) and Indigenous Knowledge holders, who play a vital role in conservation planning and implementation (KM 30.5; Ch. 16).405,425,426,427,428

URL
Alternative text
The Climate Urgency of Pacific Island Conservation
A collage of six photos are titled the Climate Urgency of Pacific Island Conservation. Top left: Firefighters stand at the left of a strip of mostly bare ground with vegetation burning at the right. Top right: Four petri dishes contain snails, with a gloved hand visible at the right. Center right: two people kneel on a beach, surrounded by roosting gull-like birds; one person is lowering a small bird into a blue box. Bottom right: two underwater divers observe a coral reef. Bottom center: several people in hardhats are installing vertical poles in a line extending into the distance. Bottom left: A man squats down to insert a plant into the ground.
Conservation efforts across the region help to restore ecosystem health and protect native species.
Figure 30.14. These images depict on-the-ground climate-related conservation actions across Pacific Island ecosystems: wildfire management in Hawaiʻi Volcanoes National Park (top left); planting native species in Palau to restore watershed health (bottom left); installing protective fencing around native habitat in Hawaiʻi (bottom center); conservation of native snails using captive populations to prevent extinction of vulnerable populations (top right); seabird translocations in the Northwestern Hawaiian Islands to safeguard against sea level rise (center right); and climate-resilient coral reef restoration experiments in Hawaiʻi (bottom right). Photo credits: (top left) D. Benitiez, NPS; (top right) © Chris A. Johns; (center right) © Lindsay Young, Pacific Rim Conservation; (bottom left) © Ann Singeo, Ebiil Society Inc.; (bottom center) NPS; (bottom right) Hawaiʻi Department of Land and Natural Resources.


Indigenous Knowledge Systems Strengthen Island Resilience

Indigenous Peoples and their knowledge systems are central to the resilience of island communities amidst the changing climate . Reciprocal and spiritual relationships among the lands, territories, waters, resources, and peoples are being strengthened and sustained as communities adapt and manage their resources collectively . Indigenous Peoples are identifying and quantifying the potential loss and migration of critical resources and expanding the cultivation of traditional food crops on high islands .

Reciprocal Relationships Between People and Place

Communities throughout Hawaiʻi and the USAPI demonstrate Indigenous cultural and community resilience grounded in Traditional Knowledge as they continue to adapt to global changes, just as their ancestors have for millennia (KM 18.3; Figure 16.3).87 These adaptations and the collective resilience of Indigenous communities are strengthened and sustained through reciprocal exchanges between the peoples and the lands, territories, waters, and resources to which they are genealogically connected (Figure 30.15). Resilient communities are vital to the overall health and well-being of island peoples. To effectively advance the science of sustainability and manage resources amidst the changing climate, spiritual rituals and engagements are central to biocultural well-being—the collective well-being of landscapes, seascapes, and Indigenous communities (Box 30.6).429 Through these rituals and engagements, island communities individually and collectively are able to connect to the place and all of its life-forms, cultivating reciprocal relations that enhance future resource abundance based on responsibility rather than ownership.430

URL
Alternative text
Restoring and Caring for Hawaiian Limu (Seaweed)
A collage titled restoring and caring for Hawaiian Limu (seawood) includes two photos. At left, yellowish-green seawood covers almost the entire surface of rock. At right, patches of light green and dark green seaweed glisten with moisture along a rocky shoreline with tidal pools.
The resilience of Pacific Island communities is strengthened by their connection to place and all of its life-forms.
Figure 30.15. Limu refers to ocean plants, including seaweed. The governor of Hawaiʻi designated 2022 as the Year of the Limu as a part of a statewide community effort to raise awareness about the importance of limu to Hawaiʻi’s cultural identity and the health of the nearshore marine environment. The KUA Limu Hui (a seaweed practitioners group) shares traditional knowledge and practices related to limu gathering, use, and restoration. Limu kala (Sargassum echinocarpum; left) is incorporated into various food dishes, is used as bait for reef fish, and is an important component in Hawaiian forgiveness ceremonies. Limu such as palahalaha (Ulva fasciata; right) also play a critical role in intertidal ecosystems as they provide food and shelter for invertebrates and herbivores. Photo credits: © Haunani Kane.

Box 30.6. Local Cultural Resilience to Climate Change

Communities across the region are working to build local cultural resilience to climate change. In Hawaiʻi, community-based subsistence fishing431 and forest432 areas were established as place-based approaches to strengthen communities’ ability to formally manage their natural resources through traditional and customary skills, practices, and social networks. Communities are cultivating reciprocal relationships as a shared responsibility433 and including sacred relationships and ritual approaches to land and sea stewardship.429 In Hawaiʻi, a common practice within the community is to ask for permission to physically and spiritually enter a sacred space, as this allows community members to introduce their genealogies to the lands and people, as well as express gratitude and respect for the land—the elder sibling—to sustain future generations.

Cultural and Historical Sites

Archaeological, cultural, and historical sites are representations of the living culture and ancestral knowledge of Indigenous and island peoples, and they serve as potential resources and models as communities seek to remediate increasing climate risks and impacts (Figure 30.16).87,118,119,434 Indigenous communities are identifying and protecting cultural and historical sites, assessing climate impacts on natural resources, and creating restoration plans (KM 16.3).435,436

Archaeological sites and oral history document the culturally grounded and traditional resilience of island peoples to historical coastal change that resulted from extreme events and higher sea levels. Approximately 2,000–4,000 years ago across the equatorial Pacific, sea level was at least 3.3–6.6 feet higher than present, which directly influenced the timing of atoll formation and the initial migrations and settlement of island people.437 Initial settlers of Majuro atoll, RMI, arrived within 100 years of island formation, when sea level was 3.3 feet higher than present, and they cultivated trees and shrubs into crop systems rather than waiting for natural vegetation succession.438 On Yap, FSM, coastal stone-built structures are expressions of innovation, cultural identity, and pride that allowed islanders to occupy coastal areas under elevated sea level, and modern structures such as the coastal men’s houses (faluw) and taro gardens document cultural resistance to rising waters.87 On Guam, traditional CHamoru houses were elevated on limestone pillars (latte) along the coast, protecting them from coastal inundation.439 Across higher islands like Sāmoa, settlement along narrow coastal plains occurred after nearly 1,000 years of sea level fall and subsequent natural development of habitable coastal environments.437 The oral histories, stories, myths, storyboards (Palau), and songs/chants of Indigenous Peoples record their observations of the changing environments and lifestyles. The proverb He pūkoʻa kani ʻāina describes the natural evolution of a coral reef into an island and is also interpreted by Native Hawaiians to describe the resilience of a person who begins in a small way and gains steadily until she becomes firmly established.440

URL
Alternative text
Climate Change Impacts on Cultural Sites
A collage titled climate change impacts on cultural sites includes two photos. At left, waves crash over structures on the shore. At right, a number of small rocks project from murky standing water, with lush green vegetation in the background.
Cultural sites, representing the living culture and ancestral knowledge of Indigenous Peoples, are at increasing risk.
Figure 30.16. Sea level rise (SLR), strong winds, and large storm waves impact a fishpond in Kaloko-Honokōhau, Hawaiʻi (left). Kukau El Bad, a cultural site in Ngarchelong State, Palau, is inundated by salt water and continues to be threatened by SLR, storm surge, and erosion (right). Photo credits: (left) © Kimberly Crawford; (right) © Ann Singeo, Ebiil Society Inc.

Across the region, one approach to mediating climate impacts is to reinvigorate and restore food production across landscapes (KMs 11.1, 30.1; Box 30.4).441 This is being accomplished through several pathways. At a policy level, work is being done to amend law in Hawaiʻi to add a “Traditional Lands” zone under the state’s Land Use Commission that would streamline permit and building requirements194 for eco-village-type living with mixed-use housing and other sustainable infrastructure such as commercial kitchen and food-processing facilities, as well as the use of traditional agriculture lands such as loʻi kalo (irrigated taro, agriculture), loko iʻa (fishponds), and large expanses used to traditionally farm staple crops such as ‘uala (sweet potato).442 Communities and cultural practitioners are working with scientists to identify areas where food production could be expanded under future climate scenarios (KM 12.4). For example, taro cultivation was modeled under future SLR scenarios434 and sweet potato442 and breadfruit under increasing temperature and rainfall scenarios,118 showing the potential resilience of these traditional agricultural practices.

Indigenous Knowledge Systems and Values of Ecosystem Services

Indigenous island communities are also working to ensure that Traditional Knowledge is central to resilience strategies (KM 16.3). A growing body of Indigenous-led research describes how biocultural methods can successfully be incorporated into efforts focused on community-based subsistence,431,432 relationships to place,433 cultural–ecosystem service assessments,443 and the protection of historical and cultural resources.444 Biocultural approaches start with and build upon local cultural perspectives by encompassing values, knowledge, and needs and by recognizing reciprocal restoration between ecosystems and human well-being (KM 20.3).195,443 The act of restoring ecosystem services contributes to cultural revitalization433 by reaffirming connection to place, enhancing community relationships and social networks and the physical and mental well-being of Indigenous Peoples,405 increasing local food production,202 and diversifying the local economy427—all while distributing the abundance through reciprocal exchange.431 In return, the renewal of culture promotes the restoration of ecological integrity through the creation and expansion of habitat for native species434 and further supports recovery and resilience of ecosystems following future environmental disturbances (KM 8.3).445 Equitable outcomes from climate research and planning are predicated on properly citing Indigenous elders and knowledge keepers,446 enhancing Indigenous control of Indigenous data via data sovereignty, protecting intellectual property rights, and establishing free, prior, and informed consent (KMs 16.2, 20.2, 31.2).447,448


TRACEABLE ACCOUNTS

Process Description

To build the author team, the federal coordinating lead author and the regional chapter lead author utilized the Fourth National Climate Assessment (NCA4) Key Messages and their assessment of new emerging issues to select key sectors of importance to the region. The lead authors compiled a comprehensive list of potential authors with expertise in those sectors. The regional chapter lead author then selected a total of 14 authors to join the team, representing a wide range of geographical and technical expertise (including physical and social scientists as well as cultural practitioners) and a diversity of career stages, affiliations (federal, academic, and private), and previous assessment experience.

The author team met weekly (virtually) to discuss chapter content and plan engagement activities. After brainstorming and agreeing on the five key topic areas for the chapter, authors identified which sections they would contribute to and met regularly in subgroups to discuss content. The team held a virtual public engagement workshop on January 24, 2022, to solicit public feedback on the chapter outline. In addition, the author team held five virtual technical meetings (one for each topic) where technical experts were invited to brainstorm and collect information to ensure the chapter covered the latest scientific results and most important topics in the region. The author team utilized interactive engagement tools to facilitate meetings, including collaborative writing exercises. Participants who contributed significantly to shaping chapter content were invited as technical contributors. Inputs from the workshop and technical meetings were synthesized by the author team and incorporated into the chapter draft.

Throughout this chapter, future projections of the physical environment come from general circulation models and earth system models from the fifth and sixth Coupled Model Intercomparison Projects (CMIP5449 and CMIP6450). 


KEY MESSAGES

KEY MESSAGE 30.1

Climate Change Impairs Access to Healthy Food and Water

Access to clean, fresh water and healthy food is expected to be increasingly impaired by climate change . On low-lying atolls, sea level rise has caused saltwater contamination of fresh water . Regionally, food and water availability will be further negatively impacted by increasing temperatures, altered rainfall patterns, increased flooding and pollution, and degradation of nearshore fisheries . Adaptation actions such as traditional farming, fishing, and land-management practices can help build more resilient water and food systems .

Read about Confidence and Likelihood

Description of Evidence Base

Global assessments support findings that coastal land loss attributable to sea level rise (SLR), increased precipitation, wave impacts, and increased aridity drive food and water insecurity on small islands.89 Regional literature shows decreasing water quality and food production in both observed trends and modeled projections (KM 11.1).77,135,147 However, these climate change manifestations are highly variable across different islands and within islands. Limited studies (e.g., Denton et al. 2014; Felton 2021; Ghazal et al. 2019; Jarsjö et al. 2020; Kibria et al. 2021; Leta et al. 2017, 2018; Mair et al. 2019; Strauch et al. 2014, 2015, 2018140,141,144,145,146,147,151,152,154,155,451) have quantified these effects on water resources and water quality throughout the large and diverse region. Although available studies and their results may be applicable to other, understudied islands, given the high diversity among islands, additional site-specific assessments in the Pacific Islands region would improve understanding of the impacts of climate change on water.

The importance of fisheries and agriculture for nutrition and livelihoods, and the nexus between food, trade, and malnutrition, come from a well-established evidence base,31,32,165,175,191,199,255,452,453 although localized assessments dissecting socioeconomic–ecological dynamics remain limited.166,199 Clear evidence shows that local agricultural and fisheries production is not keeping up with population, with outputs falling due to climate change.31,452,454

It is clear that fish, and particularly reef fish, are essential for regional nutrition and food security.82,177,183 Evidence indicates that climate change is driving and will continue to drive changes to coral reefs and fisheries yields (along with pollution and overharvest).78,81,113

A broad literature base clearly establishes strong connections between drought and water security, sanitation, food productivity, and increased risk of wildfires.191,217 Although few studies assess regional changes in drought,49,50 Hawaiʻi has clearly experienced a drying trend,48 particularly since the 1950s in La Niña years.149,150

It is generally agreed that reinvigorating local agricultural and marine food systems will be necessary, but not sufficient, for food security116,175,190 and that investment in climate-resilient food supply chains is needed.166,167,176

Major Uncertainties and Research Gaps

Global and downscaled projections of rainfall exhibit large uncertainty in direction and magnitude of future change (e.g., Elison Timm et al. 2015; Xue et al. 2020; Zhang et al. 2016 51,57,455). Island-specific downscaled projections of hydrometeorological extremes (drought, flooding, heavy precipitation) are not currently available for Hawaiʻi or the US-Affiliated Pacific Islands (USAPI). Understanding of future groundwater availability is limited by the lack of island-specific groundwater models for islands outside of the main Hawaiian Islands, some atolls in the Federated States of Micronesia, and Guam (e.g., Bailey et al. 2008; Gingerich 2013; Izuka et al. 2021456,457,458). Very little research exists regarding enhanced mobilization of subsurface contaminants from rising sea levels, despite the existence of many coastal contamination sites. Watershed management could be improved through better understanding of the current impacts of invasive plants (e.g., strawberry guava, Psidium cattleianum) on evapotranspiration and water cycling, and of how future climate change will modify such impacts.

Localized food supply chain vulnerability assessments are lacking (e.g., Dyer 201832). Salt tolerance in many key agricultural plants is still not well understood (e.g., Palanivel and Shah 2021198), nor are the interactions between climate change and invasive agricultural pests. Reliable fish consumption information is not disaggregated by socioeconomic demographics nor by fish type, precluding analysis of nutrition (and risk from contaminants) by group. Barriers to and opportunities for reinvigorating local food systems are localized and require further analysis.

Description of Confidence and Likelihood

There is very high confidence that climate change will impair future access to clean and fresh water and healthy food. Broad global and regional literature support the finding that future water access will be compromised by reduced water availability, compromised water quality (KMs 2.2, 4.1),26,103,138,139,140 and saltwater contamination, which has already been exacerbated by SLR, especially on atolls (high confidence).98,135,136 The literature agrees that climate change will disrupt global food imports and supply chains through declines in nearshore and open-ocean fish stocks in the Pacific,31,81,109,165,166,167,168,169,177,178,179 increased crop disease,77,191 and drought.49,103

There is very high confidence that food and water availability will be negatively impacted by increasing temperatures, altered rainfall, flooding, pollution, and fisheries degradation. This confidence assessment is demonstrated by numerous peer-reviewed studies, robust global climate projections, and observations of changes to crop yields, fisheries, and freshwater ecosystems (e.g., Frazier et al. 2019; Ghazal et al. 2019; Leta et al. 2017, 2018; Mair et al. 2019; Strauch et al. 2014, 2015, 2018103,140,141,144,145,146,147,451). Based on a broad evidence base including peer-reviewed literature and Indigenous Knowledge, there is very high confidence that adaptation actions such as traditional farming, fishing, and land management practices can help build more resilient water and food systems.73,116,119,175,194,195,202,203,204,205

KEY MESSAGE 30.2

Climate Change Undermines Human Health, but Community Strength Boosts Resilience

Climate change undermines the place-based foundations of human health and well-being in the Pacific Islands . Climate shocks and stressors compromise healthcare services and worsen long-standing social and economic inequities in both mental and physical health , and these negative impacts are expected to increase in the future . Adaptation efforts that build upon existing community strengths and center local and Indigenous Knowledge systems have great potential to boost resilience .

Read about Confidence and Likelihood

Description of Evidence Base

Multiple assessments find an increasing trend in people affected or killed by climate-related disasters and extreme weather events worldwide.220,221 While health infrastructure exposure to climate risk is well documented globally, few vulnerability assessments for islands, territories, and states in the Pacific (e.g., Greene and Skeele 2014223) have examined health infrastructure vulnerability. Just one study of medical facility vulnerability was found; it included an analysis of medical facility locations in 14 Pacific Island countries, including in FSM, the Republic of the Marshall Islands, and Palau.104

There is significant evidence in the international Pacific Islands region that the current and future projected impacts of climate change are negatively affecting peoples’ mental health, although studies are lacking specifically in Hawaiʻi and the USAPI. Evidence also indicates that impacts are more severe for Indigenous Peoples because their central identity is tied to an ancestral place. Studies linking climate impacts directly to mental health outcomes point to strong differences in how mental health impacts are experienced among different populations.105,239,240,241,242 There is general agreement on the benefits of tailoring mental health services for Pacific Islanders to the specific needs of the population, including different services for migrants who have voluntarily or non-voluntarily migrated.237,243

There is strong evidence of the high prevalence and impact on human health of vector-borne disease in the Pacific Islands. Recent data from 2014 to 2020 document 104 dengue, chikungunya, and Zika outbreaks across Pacific Island countries and areas.246 Literature agrees that the viruses had unexpected virulence and epidemic potential245,247 and that future climate-driven spread and emergence of vector-borne diseases the Pacific region is expected.247,249

Multiple lines of evidence demonstrate the impacts of high and extreme temperatures on human health.220,459 Substantial and growing evidence supports the disproportionate and acute effects of heat on vulnerable populations.220 However, analysis of the burden of heat-related illness and death among specific populations in Hawaiʻi and the Pacific Islands is lacking.

Social and community adaptive capacity has a long history and broad disciplinary foundations, with many studies specific to Pacific Island countries and territories highlighting the importance of social capital, cultural norms, Traditional and Indigenous Knowledge, and women’s voices in successful adaptation and disaster response (e.g., Bryant-Tokolau 2018; Cinner and Barnes 2019; Cohen et al. 2016; McNamara et al. 2020; Nunn et al. 2020; Warrick et al. 2017260,321,460,461,462,463).

The literature on necessary adaptations for Pacific Island public health systems is relatively underdeveloped compared to the global literature on the topic. For example, a study of Organization for Economic Co-operation and Development countries’ national-level public health adaptation found a diverse array of adaptations related to cross-sectoral collaboration, vertical coordination, and national health adaptation planning.264 Two studies focus on needed adaptations in the Pacific Islands,227,265 while the World Health Organization267 produced national climate change and health vulnerability assessments to guide health system adaptation plans.

Major Uncertainties and Research Gaps

Trends and changes in climate extremes in the USAPI represent a current research gap. Studies that account for compound or cascading extremes can best inform planning. Extreme event attribution studies for Pacific Islands and Hawaiʻi would improve confidence and understanding of the role of climate change in driving societal impacts from extreme weather and climate events. The region lacks site-specific vulnerability assessments for critical health infrastructure. Dynamic inundation models that include wave-driven flooding and future scenario planning tools for coral reef–protected shorelines can improve understanding of health infrastructure vulnerability.

Few studies specifically investigate climate change impacts on mental health in Hawaiʻi and the USAPI, which, given the evidence that effective interventions must be culturally appropriate and tailored, indicates a strong need for additional research. Few studies in the region specifically address the mental health impacts of climate-induced migration on displaced populations. New research can point to ways to build personal resilience to climate change among frontline workers and climate adaptation practitioners, a topic preliminary research has examined.464

Changes in climate are expected to exacerbate the increasing risk of vector-borne disease transmission throughout the region, and various species of invasive mosquitoes are already linked to outbreaks of Zika, chikungunya, and dengue. The ways in which climate change will affect disease emergence are complex and yet to be fully explored. Place-based surveillance to assess the association between climate factors and infections, as well as climate early warning systems for vector-borne disease, would help better understand and prevent epidemics.

Regional stakeholders have called for community-based approaches to research assessing climate change readiness. Such research may include assessments of community strengths and local knowledge, community-led pilot initiatives, and identification of priorities for climate resilience planning.27 

Description of Confidence and Likelihood

There is high confidence that warming temperatures, impacts from tropical cyclones, food and freshwater insecurity, and flooding are already negatively impacting human health in the Pacific Islands region. This is based on agreement among multiple lines of evidence, including peer-reviewed publications and reports and national and regional government reports, that show increases in heat-related illness and vector-borne diseases, damage to critical infrastructure, and psychological stress. Documented impacts to critical electric, medical, and transit infrastructure provide evidence that healthcare services have been compromised, although formal assessments of regional healthcare infrastructure are lacking, resulting in an assignment of medium confidence. Data linking local climate impacts such as drought and flooding with negative direct and indirect health outcomes in different communities in the international Pacific Islands demonstrate that there is high confidence that these impacts have worsened existing health inequities in both physical and mental health across the region. Based on current scientific consensus, there is very high confidence that the drivers of the negative impacts of climate change, such as high temperatures and SLR, are expected to worsen in the future. Meta-studies show that examples of health and disaster adaptations and recovery that center Indigenous ways of knowing and social cohesion have had success in the region, and there is high confidence that expanding these activities will increase resilience.

KEY MESSAGE 30.3

Rising Sea Levels Threaten Infrastructure and Local Economies and Exacerbate Existing Inequities

Climate change, particularly sea level rise (SLR), will continue to negatively impact the built environment and will harm numerous sectors of the islands’ economies . SLR intensifies loss of territory and exclusive economic zones, particularly in low islands . Climate-driven changes will exacerbate existing social challenges by disrupting livelihoods . Adaptation to climate change and recovery from disasters is logistically challenging and disproportionately more expensive in the islands . Government and community groups have developed innovative ways to reduce emissions and improve resilience by moving toward renewable energy and green infrastructure, nature-based urban planning, forward-looking building codes, and sustainable and equitable economic growth, guided by Western science and Traditional Knowledge.

Read about Confidence and Likelihood

Description of Evidence Base

The finding that climate change, especially SLR, will continue to negatively impact buildings, infrastructure, and the built environment is based on future projections of SLR (App. 3) encompassed in a suite of scenarios that include physical and socioeconomic factors from Sweet et al. (2022).65 Available literature agrees that wave-driven flooding and high sea level events and associated inundation will continue to increase in frequency and severity.98,218,219,465 There is scientific consensus that tropical cyclone (TC) intensity is increasing globally with warming.70,216 One study of TC changes shows a likelihood of fewer but possibly stronger storms (increasing maximum intensities) in the northwestern Pacific.53

Mycoo et al. (2022)89 have extensively documented the impacts of SLR, heavy rain events, TCs, and storm surges on the coastal built environment and rural communities on small islands. The primary sources of economic data for Freely Associated States are the Asian Development Bank, the World Bank (2022b);22 United Nations, and the CIA World Factbook economic impact (costs) studies. Population figures and trends for American Sāmoa, the Commonwealth of the Northern Mariana Islands, Guam, and Hawaiʻi are from the US Census.19,20,21

Major Uncertainties and Research Gaps

Wave run-up models incorporating Sweet et al. (2022)65 SLR scenarios are not yet available. Needed for the development of wave run-up models are high resolution elevation and water depth data (topobathymetric information), which are currently lacking for many Pacific Islands.

The amount and timing of future SLR experienced across the region is a key area of remaining uncertainty. There is uncertainty in the physical processes—particularly marine ice sheet instability and marine ice cliff instability—that could lead to rapid ice mass loss over a period of several decades (KM 3.3).

There is uncertainty in the effectiveness of migration as a climate change adaptation strategy, as the outcomes are dependent on individual situations and there is limited evidence in the literature.69,89,466,467,468,469,470,471 Anthropological and population geography literature (e.g., Connell and Brown 2005293) for Micronesia establishes that past and present migration was an adaptation strategy associated with resource scarcity and that, historically, migrants traveled for economic and educational reasons.472 There is limited current empirical evidence of migration that includes historical records of disaster-driven displacement; projections of displacement are also not available.

There is a gap in the literature examining the linkages between climate change, transport, and tourism, as well as the impacts of ecological change and heat on tourism demand. Future economic losses and impacts to livelihoods due to climate change–driven invasive species distribution shifts are understudied. For example, recent coconut rhinoceros beetle (CRB) invasions in Guam and Hawaiʻi and impacts on coconut palms have led to economic losses and declines in aesthetic value and have threatened food security.473 Increased invasion of CRB following strong tropical cyclones is apparent,474,475 but the specific interactions between climate factors and invasions are not yet well studied. The invasive brown tree snake on Guam has caused billions of dollars in damage to infrastructure476 and causes up to 200 electrical blackouts per year,477 adding stress to Guam’s electrical grid, which is already facing compound climate stressors; the economic costs of species invasions in a changing climate are likely underestimated.

More guidance is needed on how equity, inclusion, and justice can be embedded in decision-making across the diverse governance arrangements in the region.478

Research on nature-based solutions has improved considerably,322,479,480 although there is limited research evaluating the benefits, economic efficiency, and long-term effectiveness of these solutions.89,481,482 Recent literature has examined the effectiveness of protection services that mangroves provide, which has important implications for long-range adaptation planning on islands (e.g., Saintilan et al. 2020; Sasmito et al. 2016; Zeng et al. 2021355,483,484).

Description of Confidence and Likelihood

It is very likely and there is high confidence that SLR will continue to damage the coastal built environment in the Pacific Islands region. This is documented by multiple lines of evidence, including peer-reviewed literature, planning documents, models, and government reports analyzing flooding, erosion, and wave impacts on coastal infrastructure across the region.

It is very likely and there is high confidence that climate impacts, including SLR, drought, and storms, will impact key economic sectors, such as tourism and fisheries. These likelihood and confidence assignments are based on peer-reviewed literature, strategic planning documents, development bank reports, and government reports detailing the projected impacts on and understanding of the behavioral, logistical, and biological features of these economic sectors.

There is high confidence of the potential for loss of territory and maritime entitlements, particularly in low islands, based on models, reports from governments, international financial institutions, and international meetings.

It is likely and there is medium confidence that climate-driven changes will exacerbate existing social challenges, thereby disrupting livelihoods. Evidence related to livelihoods disruptions under future scenarios remains sparse and will vary across contexts, thus the assignment of medium confidence. High confidence in the higher costs of adaptation and disaster recovery in islands is based on various factors that characterize islands, including geographic isolation (e.g., ASCE 2020224), reliance on imported materials and labor, vulnerable infrastructure, and sensitive ecosystems.

KEY MESSAGE 30.4

Responses to Rising Threats May Help Safeguard Tropical Ecosystems and Biodiversity

The structure and composition of Pacific Island coastal and marine ecological communities are directly threatened by rising ocean temperatures, ocean acidification, and sea level rise . Increasingly severe droughts and warming are increasing fire risk and will have broad negative impacts on native plants and wildlife, including an increased risk of forest bird extinctions . Adaptation strategies improve the resilience of ecosystems, including ecosystem protection, ecological restoration, invasive species prevention and control, and investments in fire prevention .

Read about Confidence and Likelihood

Description of Evidence Base

Based on consensus across the cited literature and the latest available climate projections, there is high confidence across all future scenarios that deteriorating climate conditions will continue to threaten regional ecosystems and biodiversity throughout the this century (e.g., Buffington et al. 2021; Eakin et al. 2019; Fortini et al. 2015; Gove et al. 2022; Jacobi and Warshauer 2017; Kwiatkowski et al. 2020; Liao et al. 2015; Lotze et al. 2019; Reynolds et al. 2015; Palacios-Abrantes et al. 202260,61,62,83,86,93,94,331,354,356).

Projections of how physical changes will affect ecosystems come from a range of approaches: ecosystem and food web modeling, statistical modeling, and extrapolations from change already observed. Despite the data inequities present across the region (Box 30.1), there are multiple observations documenting past and ongoing changes in marine and terrestrial ecosystems and their physical environments (e.g., Dendy et al. 2022; Judge et al. 2021; Raymundo et al. 2019229,334,414).

Major Uncertainties and Research Gaps

The adaptive capacity of organisms and ecosystems in the face of climate change remains uncertain. For example, there is uncertainty about the plankton community’s response to climate change, which will influence the effect of climate change on higher-trophic-level organisms such as those targeted by subsistence, commercial, and recreational fisheries. Ecosystem response to simultaneous stressors and novel climate conditions is a complex subject area with high uncertainty. The effects of climate change on fish stocks outside the EEZs are underexplored.

While regional climate projections and historical climate analyses for Hawaiʻi have been developed, similar sets of studies for USAPI are much more limited, lowering our confidence in projected terrestrial impacts of climate in other US-affiliated jurisdictions (e.g., future wildfire probabilities).377 This gap in available climate data and projections is paralleled in the Caribbean region (KM 23.2), indicating a broad uncertainty for the future of our Nation’s island areas.

The impacts of extreme events on Pacific Island terrestrial ecosystems are still poorly studied given the limited data to characterize past and current events and project future shifts in intensity and frequency of such events. These uncertainties in extreme event impacts on island ecosystems are similar to those identified in the Caribbean chapter (see Traceable Account, KM 23.2), highlighting a common challenge faced by underserved island areas.

The societal response to regional climate impacts can have a large impact on surrounding ecosystems and is also a major area of uncertainty.

Description of Confidence and Likelihood

There is high confidence and it is very likely that the structure and composition of Pacific Island coastal and marine ecological communities are directly threatened by ocean changes. This assessment is based on similarities across climate scenarios through the mid-21st century, as well as on the degree to which climate conditions have already impacted regional ecosystems and biodiversity, and given species-specific climate and habitat tolerances.

Fire is already a substantial challenge to Pacific Islands (Figure 30.13),229,378 with risks expected to rise under additional warming and drying (high confidence).377 A wide body of literature links increasing droughts and temperatures to increased fire risk (Chs. 7, 8).

Regarding native plants, climatic shifts have already been shown to influence plant communities, from broad landscape shifts to individual species population trends (very likely, high confidence).364,365,366,370 Future projections indicate continued and drastic effects.93,367 Regarding forest birds and other wildlife, the link between forest bird declines in Hawaiʻi and warming is clear,414,415 with underlying mechanisms well understood.485,486 These declining trends are consistently projected to continue under additional warming (very likely, high confidence).93,94

There is medium confidence in the ability of certain adaptation strategies to improve the resilience of Pacific Island ecosystems. Ecological restoration efforts and invasive species prevention, eradication, and control enhance regional climate resilience and provide multiple benefits to islands (e.g., KM 8.3; Barbosa and Asner 2017; Bremer et al. 2018; Ferrario et al. 2014; Wada et al. 2017202,289,398,401), including helping to reduce water stress and fire risk (e.g., KM 8.2; Dudley et al. 2020; Fortini et al. 2021; Strauch et al. 2017; Trauernicht 2019148,377,380,388). However, due to the uncertainties in regional projections and climate and invasive species interactions, there is medium confidence in restoration and invasive species control efforts. The establishment and management of protected areas are also widely considered effective components of ecological adaptation strategies,119 but large climatic shifts may reduce their effectiveness over time,399 leading to medium confidence in their long-term effectiveness. Fire management strategies have been shown to be quite effective across the Pacific Islands region.125 However, the effectiveness of these strategies under extreme fire conditions is expected to be reduced (e.g., atypically high wind and dry conditions), thus medium confidence.

KEY MESSAGE 30.5

Indigenous Knowledge Systems Strengthen Island Resilience

Indigenous Peoples and their knowledge systems are central to the resilience of island communities amidst the changing climate . Reciprocal and spiritual relationships among the lands, territories, waters, resources, and peoples are being strengthened and sustained as communities adapt and manage their resources collectively . Indigenous Peoples are identifying and quantifying the potential loss and migration of critical resources and expanding the cultivation of traditional food crops on high islands .

Read about Confidence and Likelihood

Description of Evidence Base

There is no doubt that fostering reciprocal relationships between people, place, and cultural and historical sites across Hawaiʻi and the USAPI is central to the ongoing adaptation of island communities to the changing climate (e.g., Diver et al. 2019; Nunn et al. 201787,430). However, these types of relationships are usually documented in an oral rather than written format. For the most part, there is agreement that the culture of Indigenous Peoples influences their interpretation of the value of place and ecosystems and, subsequently, their resilience to climate change. The studies cited in this section use the Intergovernmental Panel on Climate Change (IPCC) Fifth Assessment Report CMIP5 results for temperature, rainfall, and SLR to assess impacts on traditional foods and cultural resources.118,434,442

Major Uncertainties and Research Gaps

Research that assesses the impacts of climate change (SLR, temperature, etc.) on cultural resources and historical sites is limited and largely focused on Hawaiʻi. Many of the studies that assess climate-related impacts to cultural resources were published prior to the release of the updated IPCC Sixth Assessment Report and NOAA’s updated SLR projections. There is limited information on how climate change–driven shifts in the distributions of invasive plants and animals may disrupt cultural services and familial relationships (e.g., Brewington et al. 2023359).

Description of Confidence and Likelihood

Literature focused on community and place-based approaches to natural resource management supports that there is high confidence that Indigenous Peoples of the Pacific Islands, their knowledge systems, and their rituals are central to local climate resilience. Literature also supports that there is high confidence that reciprocal and spiritual relationships among people and place are being strengthened through adaptation and collective management of resources.

There is high confidence that the application of future climate scenarios has enabled the collective efforts of Indigenous researchers, stakeholders, and scientists to begin to identify and quantify the potential loss and migration of critical resources and expand the cultivation of traditional food crops on high islands. However, such assessments are limited in scope across Hawaiʻi and the USAPI, and as a result the impacts of climate change on cultural resources are still identified as a major gap in knowledge.

REFERENCES

  1. Finney, B., 1997: Pacific Islanders at sea. American Anthropologist, 99 (2), 403–404. https://doi.org/10.1525/aa.1997.99.2.403

  2. Clarke, W.C. and R.R. Thaman, Eds., 1993: Agroforestry in the Pacific Islands: Systems for Sustainability. United Nations University Press, 307 pp. https://archive.unu.edu/unupress/unupbooks/80824e/80824e00.htm
  3. Falanruw, M.V.C., 1993: Micronesian agroforestry: Evidence from the past, implications for the future. In: Proceedings of the Workshop on Research Methodologies and Applications for Pacific Island Agroforestry; July 16–20, 1990; Kolonia, Pohnpei, Federated States of Micronesia. Raynor, B. and R.R. Bay, Eds. Pacific Southwest Research Station, Forest Service, U.S. Department of Agriculture, Albany, CA, 37–41. https://www.srs.fs.usda.gov/pubs/27382
  4. Manner, H.I., 1993: A review of traditional agroforestry in Micronesia. In: Proceedings of the Workshop on Research Methodologies and Applications for Pacific Island Agroforestry; July 16–20, 1990; Kolonia, Pohnpei, Federated States of Micronesia. Raynor, B. and R.R. Bay, Eds. Pacific Southwest Research Station, Forest Service, U.S. Department of Agriculture, Albany, CA, 32–36. https://www.fs.usda.gov/research/treesearch/27381
  5. Raynor, B. and J. Fownes, 1993: An Indigenous Pacific Island agroforestry system: Pohnpei Island. In: Proceedings of the Workshop on Research Methodologies and Applications for Pacific Island Agroforestry; July 16–20, 1990; Kolonia, Pohnpei, Federated States of Micronesia. Raynor, B. and R.R. Bay, Eds. Pacific Southwest Research Station, Forest Service, U.S. Department of Agriculture, Albany, CA, 42–58. https://www.fs.usda.gov/research/treesearch/27383
  6. Falanruw, M.V.C., 1994: Traditional fishing in Yap. In: Science of Pacific Peoples: Ocean and Coastal Shores. Bluebird Printery, Suva, Fiji, 41–58. [Print].
  7. Johannes, R.E., 1978: Traditional marine conservation methods in Oceania and their demise. Annual Review of Ecology and Systematics, 9 (1), 349–364. https://doi.org/10.1146/annurev.es.09.110178.002025
  8. Johannes, R.E., 1981: Words of the Lagoon: Fishing and Marine Lore in the Palau District of Micronesia. University of California Press, Berkeley, CA. https://georgehbalazs.com/wp-content/uploads/2019/05/1981-WORDS-OF-THE-LAGOON-FISHING-MARINE-LORE-IN-THE-PALAU-DISTRICT-OF-MICRONESIA-EPILOGUE-PREFACE-ACKNOWLEGEMENTS-INDEXED-PAGES-FOR-TURTLES-1.pdf
  9. Taafaki, I.J., M.K. Fowler, and R.R. Thaman, 2006: Traditional Medicine of the Marshall Islands: The Women, the Plants, the Treatments. University of the South Pacific, Institute of Pacific Studies, 300 pp. https://books.google.com/books/about/Traditional_Medicine_of_the_Marshall_Isl.html?id=xBxbCLXGwQkC
  10. Elliott, M., M.C. MacDonald, T. Chan, A. Kearton, K.F. Shields, J.K. Bartram, and W.L. Hadwen, 2017: Multiple household water sources and their use in remote communities with evidence from Pacific island countries. Water Resources Research, 53 (11), 9106–9117. https://doi.org/10.1002/2017wr021047
  11. Poyer, L., 1991: Ch. 7. Micronesian experiences of the War in the Pacific. In: Remembering the Pacific War. White, G.M., Ed. Center for Pacific Islands Studies, School of Hawaiian, Asian, and Pacific Studies, University of Hawai‘i at Mānoa, Honolulu, HI, 79–89. http://hdl.handle.net/10125/15555
  12. Cocklin, C., 1999: Ch. 9. Islands in the midst: Environmental change, vulnerability, and security in the Pacific. In: Environmental Change, Adaptation, and Security. Lonergan, S.C., Ed. Springer, Dordrecht, Netherlands, 141–159. https://doi.org/10.1007/978-94-011-4219-9_9
  13. Simon, S.L., 1997: A brief history of people and events related to atomic weapons testing in the Marshall Islands. Health Physics, 73 (1). https://doi.org/10.1097/00004032-199707000-00001
  14. Spencer, M.S., T. Fentress, A. Touch, and J. Hernandez, 2020: Environmental justice, Indigenous knowledge systems, and Native Hawaiians and other Pacific Islanders. Human Biology, 92 (1), 45–57. https://doi.org/10.13110/humanbiology.92.1.06
  15. Keener, V., J.J. Marra, M.L. Finucane, D. Spooner, and M.H. Smith, Eds., 2012: Climate Change and Pacific Islands: Indicators and Impacts. Report for The 2012 Pacific Islands Regional Climate Assessment. Island Press, Washington, DC. https://www.reefresilience.org/pdf/NCA-PIRCA-FINAL.pdf
  16. U.S. Census Bureau. 2013: 2010 Island Areas - American Samoa Dataset. U.S. Department of Commerce, U.S. Census Bureau. https://www.census.gov/data/datasets/2010/dec/american-samoa.html
  17. U.S. Census Bureau. 2013: 2010 Island Areas - Commonwealth of the Northern Mariana Islands Dataset. U.S. Department of Commerce, U.S. Census Bureau. https://www.census.gov/data/datasets/2010/dec/cnmi.html
  18. U.S. Census Bureau. 2013: 2010 Island Areas - Guam Dataset. U.S. Department of Commerce, U.S. Census Bureau. https://www.census.gov/data/datasets/2010/dec/guam.html
  19. U.S. Census Bureau, 2022: 2020 Island Areas Censuses: Guam. U.S. Department of Commerce, U.S. Census Bureau. https://www.census.gov/data/tables/2020/dec/2020-guam.html
  20. U.S. Census Bureau, 2022: 2020 Island Areas Censuses: American Samoa. U.S. Department of Commerce, U.S. Census Bureau. https://www.census.gov/data/tables/2020/dec/2020-american-samoa.html
  21. U.S. Census Bureau, 2022: 2020 Island Areas Censuses: Commonwealth of the Northern Mariana Islands (CNMI). U.S. Department of Commerce, U.S. Census Bureau. https://www.census.gov/data/tables/2020/dec/2020-commonwealth-northern-mariana-islands.html
  22. The World Bank. 2022: Agriculture, forestry, and fishing, value added (% of GDP) - American Samoa, Palau, Micronesia, Fed. Sts., Guam, Marshall Islands. World Bank Group. https://data.worldbank.org/indicator/nv.agr.totl.zs?locations=as-pw-fm-gu-mh
  23. U.S. Census Bureau, 2022: Quick Facts: Hawaii. U.S. Department of Commerce, U.S. Census Bureau. https://www.census.gov/quickfacts/fact/table/HI
  24. Semega, J. and M. Kollar, 2022: Income in the United States: 2021. P60-276. U.S. Department of Commerce, U.S. Census Bureau, Washington, DC. https://www.census.gov/library/publications/2022/demo/p60-276.html
  25. Techera, E.J., 2013: Ch. 16. Climate change, legal governance and the Pacific Islands: An overview. In: Climate Change and Indigenous Peoples. Abate, R.S. and E.A. Kronk, Eds. Edward Elgar Publishing, Cheltenham, UK, 339–362. https://doi.org/10.4337/9781781001806.00030
  26. Keener, V., D. Helweg, S. Asam, S. Balwani, M. Burkett, C. Fletcher, T. Giambelluca, Z. Grecni, M. Nobrega-Olivera, J. Polovina, and G. Tribble, 2018: Ch. 27. Hawai’i and U.S.-affiliated Pacific Islands. In: Impacts, Risks, and Adaptation in the United States: Fourth National Climate Assessment, Volume II. Reidmiller, D.R., C.W. Avery, D. Easterling, K. Kunkel, K.L.M. Lewis, T.K. Maycock, and B.C. Stewart, Eds. U.S. Global Change Research Program, Washington, DC, USA, 1242–1308. https://doi.org/10.7930/nca4.2018.ch27
  27. Grecni, Z., E.M. Derrington, R. Greene, W. Miles, and V. Keener, 2021: Climate Change in the Commonwealth of the Northern Mariana Islands: Indicators and Considerations for Key Sectors. East-West Center, Honolulu, HI. https://doi.org/10.5281/zenodo.4426942
  28. Grecni, Z., W. Miles, R. King, A. Frazier, and V. Keener, 2020: Climate Change in Guam: Indicators and Considerations for Key Sectors. East-West Center, Honolulu, HI. https://doi.org/10.5281/zenodo.4037481
  29. Keener, V., Z. Grecni, K. Anderson Tagarino, C. Shuler, and W. Miles, 2021: Climate Change in American Sāmoa: Indicators and Considerations for Key Sectors. East-West Center, Honolulu, HI. https://doi.org/10.5281/zenodo.4663397
  30. Polhemus, D.A., 2017: Drought in the U.S.-Affiliated Pacific Islands: A Multi-level Assessment. U.S. Fish and Wildlife Service, Pacific Islands Fish and Wildlife Office. https://doi.org/10.21429/c9zs74
  31. Barnett, J., 2020: Ch. 2. Climate change and food security in the Pacific Islands. In: Food Security in Small Island States. Connell, J. and K. Lowitt, Eds. Springer, Singapore, 25–38. https://doi.org/10.1007/978-981-13-8256-7_2
  32. Dyer, J., 2018: Ch. 20. Predicting true climate change risks and opportunities in the Cook Islands: How vulnerable are Pacific maritime supply chain stakeholders? In: Climate Change Impacts and Adaptation Strategies for Coastal Communities. Leal Filho, W., Ed. Springer, Cham, Switzerland, 373–408. https://doi.org/10.1007/978-3-319-70703-7_20
  33. Johnson, J.E., V. Allain, B. Basel, J.D. Bell, A. Chin, L.X.C. Dutra, E. Hooper, D. Loubser, J. Lough, B.R. Moore, and S. Nicol, 2020: Ch. 10. Impacts of climate change on marine resources in the Pacific Island Region. In: Climate Change and Impacts in the Pacific. Kumar, L., Ed. Springer, Cham, Switzerland, 359–402. https://doi.org/10.1007/978-3-030-32878-8_10
  34. McIver, L., M. Hashizume, H. Kim, Y. Honda, M. Pretrick, S. Iddings, and B. Pavlin, 2015: Assessment of climate-sensitive infectious diseases in the Federated States of Micronesia. Tropical Medicine and Health, 43 (1), 29–40. https://doi.org/10.2149/tmh.2014-17
  35. Keener, V.W., Z.N. Grecni, and S.C. Moser, 2022: Accelerating climate change adaptive capacity through regional sustained assessment and evaluation in Hawai’i and the U.S. affiliated Pacific Islands. Frontiers in Climate, 4, 869760. https://doi.org/10.3389/fclim.2022.869760
  36. OSTP, 2022: Guidance for Federal Departments and Agencies on Indigenous Knowledge. White House Office of Science and Technology Policy, Washington, DC. https://www.whitehouse.gov/wp-content/uploads/2022/12/ostp-ceq-ik-guidance.pdf
  37. Winter, K.B., M.B. Vaughan, N. Kurashima, L. Wann, E. Cadiz, A.H. Kawelo, M. Cypher, L. Kaluhiwa, and H.K. Springer, 2023: Indigenous stewardship through novel approaches to collaborative management in Hawaiʻi. Ecology and Society, 28 (1). https://doi.org/10.5751/es-13662-280126
  38. Keener, V., D. Helweg, S. Asam, S. Balwani, M. Burkett, C. Fletcher, T. Giambelluca, Z. Grecni, M. Nobrega-Olivera, J. Polovina, and G. Tribble, 2018: Box 27.1 in Ch. 27. Hawai’i and U.S.-affiliated Pacific Islands. In: Impacts, Risks, and Adaptation in the United States: Fourth National Climate Assessment, Volume II. Reidmiller, D.R., C.W. Avery, D. Easterling, K. Kunkel, K.L.M. Lewis, T.K. Maycock, and B.C. Stewart, Eds. U.S. Global Change Research Program, Washington, DC, USA, 1242–1308. https://doi.org/10.7930/nca4.2018.ch27
  39. Frazier, A.G., O. Elison Timm, T.W. Giambelluca, and H.F. Diaz, 2018: The influence of ENSO, PDO and PNA on secular rainfall variations in Hawai‘i. Climate Dynamics, 51 (5), 2127–2140. https://doi.org/10.1007/s00382-017-4003-4
  40. Mantua, N.J. and S.R. Hare, 2002: The Pacific decadal oscillation. Journal of Oceanography, 58 (1), 35–44. https://doi.org/10.1023/a:1015820616384
  41. PEAC Center, 2016: PEAC Seasonal Sea Level Outlook: Current Conditions. National Weather Service, Pacific ENSO Applications Climate Center. http://www.weather.gov/peac/sealevel
  42. Hamlington, B.D., T. Frederikse, P.R. Thompson, J.K. Willis, R.S. Nerem, and J.T. Fasullo, 2021: Past, present, and future Pacific sea-level change. Earth's Future, 9 (4), e2020EF001839. https://doi.org/10.1029/2020ef001839
  43. Sweet, W., S. Simon, G. Dusek, D. Marcy, W. Brooks, M. Pendleton, and J. Marra, 2021: 2021 State of High Tide Flooding and Annual Outlook. National Oceanic and Atmospheric Administration, National Ocean Service, Silver Spring, MD. https://tidesandcurrents.noaa.gov/publications/2021_State_of_High_Tide_Flooding_and_Annual_Outlook_Final.pdf
  44. Thompson, P.R., M.J. Widlansky, M.A. Merrifield, J.M. Becker, and J.J. Marra, 2019: A statistical model for frequency of coastal flooding in Honolulu, Hawaii, during the 21st century. Journal of Geophysical Research: Oceans, 124 (4), 2787–2802. https://doi.org/10.1029/2018jc014741
  45. Marra, J.J., G. Gooley, M.-V. Johnson, V. Keener, M. Kruk, S. McGree, J.T. Potemra, and O. Warrick, 2022: Pacific Islands Climate Change Monitor: 2021. The Pacific Islands-Regional Climate Centre Network Report to the Pacific Islands Climate Service Panel and Pacific Meteorological Council. https://doi.org/10.5281/zenodo.6965143
  46. McKenzie, M.M., T.W. Giambelluca, and H.F. Diaz, 2019: Temperature trends in Hawaiʻi: A century of change, 1917–2016. International Journal of Climatology, 39 (10), 3987–4001. https://doi.org/10.1002/joc.6053
  47. Elison Timm, O., 2017: Future warming rates over the Hawaiian Islands based on elevation-dependent scaling factors. International Journal of Climatology, 37, 1093–1104. https://doi.org/10.1002/joc.5065
  48. Frazier, A.G. and T.W. Giambelluca, 2017: Spatial trend analysis of Hawaiian rainfall from 1920 to 2012. International Journal of Climatology, 37 (5), 2522–2531. https://doi.org/10.1002/joc.4862
  49. Frazier, A.G., C.P. Giardina, T.W. Giambelluca, L. Brewington, Y.-L. Chen, P.-S. Chu, L. Berio Fortini, D. Hall, D.A. Helweg, V.W. Keener, R.J. Longman, M.P. Lucas, A. Mair, D.S. Oki, J.J. Reyes, S.G. Yelenik, and C. Trauernicht, 2022: A century of drought in Hawaiʻi: Geospatial analysis and synthesis across hydrological, ecological, and socioeconomic scales. Sustainability, 14 (19), 12023. https://doi.org/10.3390/su141912023
  50. McGree, S., S. Schreider, and Y. Kuleshov, 2016: Trends and variability in droughts in the Pacific islands and Northeast Australia. Journal of Climate, 29 (23), 8377–8397. https://doi.org/10.1175/jcli-d-16-0332.1
  51. Elison Timm, O., T.W. Giambelluca, and H.F. Diaz, 2015: Statistical downscaling of rainfall changes in Hawai‘i based on the CMIP5 global model projections. Journal of Geophysical Research: Atmospheres, 120 (1), 92–112. https://doi.org/10.1002/2014jd022059
  52. Shuler, C., L. Brewington, and A.I. El-Kadi, 2021: A participatory approach to assessing groundwater recharge under future climate and land-cover scenarios, Tutuila, American Samoa. Journal of Hydrology: Regional Studies, 34, 100785. https://doi.org/10.1016/j.ejrh.2021.100785
  53. Widlansky, M.J., H. Annamalai, S.B. Gingerich, C.D. Storlazzi, J.J. Marra, K.I. Hodges, B. Choy, and A. Kitoh, 2019: Tropical cyclone projections: Changing climate threats for Pacific island defense installations. Weather, Climate, and Society, 11 (1), 3–15. https://doi.org/10.1175/wcas-d-17-0112.1
  54. Bloemendaal, N., H. de Moel, A.B. Martinez, S. Muis, I.D. Haigh, K. van der Wiel, R.J. Haarsma, P.J. Ward, M.J. Roberts, J.C.M. Dullaart, and J.C.J.H. Aerts, 2022: A globally consistent local-scale assessment of future tropical cyclone risk. Science Advances, 8 (17), 8438. https://doi.org/10.1126/sciadv.abm8438
  55. Knutson, T., S.J. Camargo, J.C.L. Chan, K. Emanuel, C.H. Ho, J. Kossin, M. Mohapatra, M. Satoh, M. Sugi, K. Walsh, and L. Wu, 2020: Tropical cyclones and climate change assessment: Part II: Projected response to anthropogenic warming. Bulletin of the American Meteorological Society, 101 (3), 303–322. https://doi.org/10.1175/bams-d-18-0194.1
  56. Seneviratne, S.I., X. Zhang, M. Adnan, W. Badi, C. Dereczynski, A.D. Luca, S. Ghosh, I. Iskandar, J. Kossin, S. Lewis, F. Otto, I. Pinto, M. Satoh, S.M. Vicente-Serrano, M. Wehner, and B. Zhou, 2021: Ch. 11. Weather and climate extreme events in a changing climate. In: Climate Change 2021: The Physical Science Basis. Contribution of Working Group I to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change. Masson-Delmotte, V., P. Zhai, A. Pirani, S.L. Connors, C. Péan, S. Berger, N. Caud, Y. Chen, L. Goldfarb, M.I. Gomis, M. Huang, K. Leitzell, E. Lonnoy, J.B.R. Matthews, T.K. Maycock, T. Waterfield, O. Yelekçi, R. Yu, and B. Zhou, Eds. Cambridge University Press, Cambridge, UK and New York, NY, USA, 1513–1766. https://doi.org/10.1017/9781009157896.013
  57. Zhang, C., Y. Wang, K. Hamilton, and A. Lauer, 2016: Dynamical downscaling of the climate for the Hawaiian Islands. Part II: Projection for the late twenty-first century. Journal of Climate, 29 (23), 8333–8354. https://doi.org/10.1175/jcli-d-16-0038.1
  58. Marra, J.J. and M.C. Kruk, 2017: State of Environmental Conditions in Hawaii and the U.S. Affiliated Pacific Islands Under a Changing Climate: 2017. National Oceanic and Atmospheric Administration, National Centers for Environmental Information. https://pirca.org/2017/11/30/state-of-environmental-conditions-in-hawaii-and-the-u-s-affiliated-pacific-islands-under-a-changing-climate-2017/
  59. WPRFMC, 2021: Annual Stock Assessment and Fishery Evaluation Report Pacific Island Pelagic Fishery Ecosystem Plan 2020. Remington, T., M. Fitchett, A. Ishizaki, and J. DeMello, Eds. Western Pacific Regional Fishery Management Council, Honolulu, HI, 410 pp. https://www.wpcouncil.org/wp-content/uploads/2021/08/Pelagic-FEP-SAFE-Report-2020_v2.pdf
  60. Kwiatkowski, L., O. Torres, L. Bopp, O. Aumont, M. Chamberlain, J.R. Christian, J.P. Dunne, M. Gehlen, T. Ilyina, J.G. John, A. Lenton, H. Li, N.S. Lovenduski, J.C. Orr, J. Palmieri, Y. Santana-Falcón, J. Schwinger, R. Séférian, C.A. Stock, A. Tagliabue, Y. Takano, J. Tjiputra, K. Toyama, H. Tsujino, M. Watanabe, A. Yamamoto, A. Yool, and T. Ziehn, 2020: Twenty-first century ocean warming, acidification, deoxygenation, and upper-ocean nutrient and primary production decline from CMIP6 model projections. Biogeosciences, 17 (13), 3439–3470. https://doi.org/10.5194/bg-17-3439-2020
  61. Eakin, C.M., H.P.A. Sweatman, and R.E. Brainard, 2019: The 2014–2017 global-scale coral bleaching event: Insights and impacts. Coral Reefs, 38 (4), 539–545. https://doi.org/10.1007/s00338-019-01844-2
  62. Gove, J.M., J.A. Maynard, J. Lecky, D.P. Tracey, M.E. Allen, G.P. Asner, C. Conklin, C. Couch, K. Hum, R.J. Ingram, T.L. Kindinger, K. Leong, K.L.L. Oleson, E.K. Towle, R. van Hooidonk, G.J. Williams, and J. Hospital, 2022: 2022 Ecosystem Status Report for Hawaiʻi. PIFSC Special Publication, SP-23-01. National Oceanic and Atmospheric Administration, National Marine Fisheries Service, Pacific Islands Fisheries Science Center, 91 pp. https://doi.org/10.25923/r53p-fn97
  63. Woodworth, P.L., A. Melet, M. Marcos, R.D. Ray, G. Wöppelmann, Y.N. Sasaki, M. Cirano, A. Hibbert, J.M. Huthnance, S. Monserrat, and M.A. Merrifield, 2019: Forcing factors affecting sea level changes at the coast. Surveys in Geophysics, 40 (6), 1351–1397. https://doi.org/10.1007/s10712-019-09531-1
  64. Merrifield, M.A. and M.E. Maltrud, 2011: Regional sea level trends due to a Pacific trade wind intensification. Geophysical Research Letters, 38 (21). https://doi.org/10.1029/2011gl049576
  65. Sweet, W.V., B.D. Hamlington, R.E. Kopp, C.P. Weaver, P.L. Barnard, D. Bekaert, W. Brooks, M. Craghan, G. Dusek, T. Frederikse, G. Garner, A.S. Genz, J.P. Krasting, E. Larour, D. Marcy, J.J. Marra, J. Obeysekera, M. Osler, M. Pendleton, D. Roman, L. Schmied, W. Veatch, K.D. White, and C. Zuzak, 2022: Global and Regional Sea Level Rise Scenarios for the United States: Updated Mean Projections and Extreme Water Level Probabilities Along U.S. Coastlines. NOAA Technical Report NOS 01. National Oceanic and Atmospheric Administration, National Ocean Service, Silver Spring, MD, 111 pp. https://oceanservice.noaa.gov/hazards/sealevelrise/sealevelrise-tech-report-sections.html
  66. Dhage, L. and M.J. Widlansky, 2022: Assessment of 21st century changing sea surface temperature, rainfall, and sea surface height patterns in the tropical Pacific islands using CMIP6 greenhouse warming projections. Earth's Future, 10 (4), e2021EF002524. https://doi.org/10.1029/2021ef002524
  67. Arslanalp, S., R. Koepke, and J. Verschuur, 2021: Tracking trade from space: An application to Pacific Island countries. IMF Working Papers, 2021 (225), 40. https://doi.org/10.5089/9781513593531.001
  68. Finkbeiner, E.M., F. Micheli, N.J. Bennett, A.L. Ayers, E. Le Cornu, and A.N. Doerr, 2018: Exploring trade-offs in climate change response in the context of Pacific Island fisheries. Marine Policy, 88, 359–364. https://doi.org/10.1016/j.marpol.2017.09.032
  69. Weir, T., L. Dovey, and D. Orcherton, 2017: Social and cultural issues raised by climate change in Pacific Island countries: An overview. Regional Environmental Change, 17 (4), 1017–1028. https://doi.org/10.1007/s10113-016-1012-5
  70. IPCC, 2021: Climate Change 2021: The Physical Science Basis. Contribution of Working Group I to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change. Masson-Delmotte, V., P. Zhai, A. Pirani, S.L. Connors, C. Péan, S. Berger, N. Caud, Y. Chen, L. Goldfarb, M.I. Gomis, M. Huang, K. Leitzell, E. Lonnoy, J.B.R. Matthews, T.K. Maycock, T. Waterfield, O. Yelekçi, R. Yu, and B. Zhou, Eds. Cambridge University Press, Cambridge, UK and New York, NY, USA, 2391 pp. https://doi.org/10.1017/9781009157896
  71. Shuler, C.K., H. Dulai, R. DeWees, M. Kirs, C.R. Glenn, and A.I. El-Kadi, 2019: Isotopes, microbes, and turbidity: A multi-tracer approach to understanding recharge dynamics and groundwater contamination in a basaltic island aquifer. Groundwater Monitoring & Remediation, 39 (1), 20–35. https://doi.org/10.1111/gwmr.12299
  72. Ichiho, H.M., F.T. Roby, E.S. Ponausuia, and N. Aitaoto, 2013: An assessment of non-communicable diseases, diabetes, and related risk factors in the territory of American Samoa: A systems perspective. Hawai'i Journal of Medicine and Public Health, 72 (5), 10. https://www.ncbi.nlm.nih.gov/pmc/articles/pmc3689461/
  73. Bell, J.D., C. Reid, M.J. Batty, P. Lehodey, L. Rodwell, A.J. Hobday, J.E. Johnson, and A. Demmke, 2013: Effects of climate change on oceanic fisheries in the tropical Pacific: Implications for economic development and food security. Climatic Change, 119 (1), 199–212. https://doi.org/10.1007/s10584-012-0606-2
  74. Feagaimaali’i, J., 2022: American Samoa experiencing massive coastal flooding. Samoa News, July 15, 2022. https://samoanews.com/local-news/american-samoa-experiencing-massive-coastal-flooding
  75. Wyte-Lake, T., S. Schmitz, R.J. Kornegay, F. Acevedo, and A. Dobalian, 2021: Three case studies of community behavioral health support from the US Department of Veterans Affairs after disasters. BMC Public Health, 21 (1), 639. https://doi.org/10.1186/s12889-021-10650-x
  76. Liske-Clark, J., 2015: Wildlife Action Plan for the Commonwealth of the Northern Mariana Islands: 2015–2025. CNMI Department of Land and Natural Resources, Division of Fish and Wildlife, Saipan, MP. https://opd.gov.mp/library/reports/cnmi-swap-2015-final.pdf
  77. Taylor, M., A. McGregor, and B. Dawson, 2016: Vulnerability of Pacific Island Agriculture and Forestry to Climate Change. Pacific Community, Noumea, New Caledonia. https://www.fao.org/family-farming/detail/en/c/432913/
  78. Bell, J., M. Batty, A. Ganachaud, P. Gehrke, A. Hobday, O. Hoegh-Guldberg, J. Johnson, R. Le Borgne, P. Lehodey, J. Lough, T. Pickering, M. Pratchett, M. Sheaves, and M. Waycott, 2009: Preliminary Assessment of the Effects of Climate Change on Fisheries and Aquaculture in the Pacific. Secretariat of the Pacific Community, 15 pp. https://library.sprep.org/sites/default/files/433.pdf
  79. Bell, J.D., A. Cisneros-Montemayor, Q. Hanich, J.E. Johnson, P. Lehodey, B.R. Moore, M.S. Pratchett, G. Reygondeau, I. Senina, J. Virdin, and C.C.C. Wabnitz, 2018: Adaptations to maintain the contributions of small-scale fisheries to food security in the Pacific Islands. Marine Policy, 88, 303–314. https://doi.org/10.1016/j.marpol.2017.05.019
  80. Bell, J.D., C. Reid, M.J. Batty, E.H. Allison, P. Lehodey, L. Rodwell, T.D. Pickering, R. Gillett, J.E. Johnson, A. Hobday, and A. Demmke, 2011: Ch. 12. Implications of climate change for contributions by fisheries and aquaculture to Pacific Island economies and communities. In: Vulnerability of Tropical Pacific Fisheries and Aquaculture to Climate Change. Bell, J.D., J.E. Johnson, and A.J. Hobday, Eds. Secretariat of the Pacific Community, 733–801. https://hdl.handle.net/20.500.12348/1067
  81. Bell, J.D., I. Senina, T. Adams, O. Aumont, B. Calmettes, S. Clark, M. Dessert, M. Gehlen, T. Gorgues, J. Hampton, Q. Hanich, H. Harden-Davies, S.R. Hare, G. Holmes, P. Lehodey, M. Lengaigne, W. Mansfield, C. Menkes, S. Nicol, and P. Williams, 2021: Pathways to sustaining tuna-dependent Pacific Island economies during climate change. Nature Sustainability, 4 (10), 900–910. https://doi.org/10.1038/s41893-021-00745-z
  82. Farmery, A.K., J.M. Scott, T.D. Brewer, H. Eriksson, D.J. Steenbergen, J. Albert, J. Raubani, J. Tutuo, M.K. Sharp, and N.L. Andrew, 2020: Aquatic foods and nutrition in the Pacific. Nutrients, 12 (12), 3705. https://doi.org/10.3390/nu12123705
  83. Palacios-Abrantes, J., T.L. Frölicher, G. Reygondeau, U.R. Sumaila, A. Tagliabue, Colette C.C. Wabnitz, and William W.L. Cheung, 2022: Timing and magnitude of climate-driven range shifts in transboundary fish stocks challenge their management. Global Change Biology, 28 (7), 2312–2326. https://doi.org/10.1111/gcb.16058
  84. Andrew, N.L., P. Bright, L. de la Rua, S.J. Teoh, and M. Vickers, 2019: Coastal proximity of populations in 22 Pacific Island countries and territories. PLoS ONE, 14 (9), e0223249. https://doi.org/10.1371/journal.pone.0223249
  85. Kumar, L. and S. Taylor, 2015: Exposure of coastal built assets in the South Pacific to climate risks. Nature Climate Change, 5 (11), 992–996. https://doi.org/10.1038/nclimate2702
  86. Buffington, K.J., R.A. MacKenzie, J.A. Carr, M. Apwong, K.W. Krauss, and K.M. Thorne, 2021: Mangrove Species’ Response to Sea-Level Rise across Pohnpei, Federated States of Micronesia. USGS Open-File Report 2021-1002. U.S. Geological Survey, 44 pp. https://doi.org/10.3133/ofr20211002
  87. Nunn, P.D., J. Runman, M. Falanruw, and R. Kumar, 2017: Culturally grounded responses to coastal change on islands in the Federated States of Micronesia, northwest Pacific Ocean. Regional Environmental Change, 17 (4), 959–971. https://doi.org/10.1007/s10113-016-0950-2
  88. Gingerich, S.B., A.G. Johnson, S.N. Rosa, M.D. Marineau, S.A. Wright, L.E. Hay, M.J. Widlansky, J.W. Jenson, C.I. Wong, J.L. Banner, V.W. Keener, and M.L. Finucane, 2019: Water Resources on Guam—Potential Impacts of and Adaptive Response to Climate Change. USGS Investigations Report 2019–5095. U.S. Geological Survey, 55 pp. https://doi.org/10.3133/sir20195095
  89. Mycoo, M., M. Wairiu, D. Campbell, V. Duvat, Y. Golbuu, S. Maharaj, J. Nalau, P. Nunn, J. Pinnegar, and O.Warrick, 2022: Ch. 15. Small islands. In: Climate Change 2022: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change. Pörtner, H.-O., D.C. Roberts, M. Tignor, E.S. Poloczanska, K. Mintenbeck, A. Alegría, M. Craig, S. Langsdorf, S. Löschke, V. Möller, A. Okem, and B. Rama, Eds. Cambridge University Press, Cambridge, UK and New York, NY, USA, 2043–2121. https://doi.org/10.1017/9781009325844.017
  90. King, R., K. Bautista, M. Higgs, and E. Leon-Guerrero, 2019: Vulnerability Assessment of Built Infrastructure near Coastal Bays Using Three Sea Level Rise Scenarios – Guam. Government of Guam. https://bsp.guam.gov/guamccva/
  91. Gordon, S., 2014: Heat illness in Hawai'i. Hawai'i Journal of Medicine & Public Health, 73 (11), 33–36. https://www.ncbi.nlm.nih.gov/pmc/articles/pmc4244899/
  92. Hawaiʻi Climate Change Mitigation and Adaptation Commission, 2017: Hawaiʻi Sea Level Rise Vulnerability and Adaptation Report. Tetra Tech, Inc. and the State of Hawaiʻi Department of Land and Natural Resources, Office of Conservation and Coastal Lands. https://climateadaptation.hawaii.gov/wp-content/uploads/2017/12/SLR-Report_Dec2017.pdf
  93. Fortini, L.B., A.E. Vorsino, F.A. Amidon, E.H. Paxton, and J.D. Jacobi, 2015: Large-scale range collapse of Hawaiian forest birds under climate change and the need 21st century conservation options. PLoS ONE, 10, e0144311. https://doi.org/10.1371/journal.pone.0140389
  94. Liao, W., O. Elison Timm, C. Zhang, C.T. Atkinson, D.A. LaPointe, and M.D. Samuel, 2015: Will a warmer and wetter future cause extinction of native Hawaiian forest birds? Global Change Biology, 21 (12), 4342–4352. https://doi.org/10.1111/gcb.13005
  95. Kauahi, C. 2018: Hydrology of Three Loko Iʻa, Hawaiian Fishponds, on Windward Hawaiʻi Island, Hawaiʻi. Master of Science in Tropical Conservation Biology and Environmental Science, University of Hawaiʻi at Hilo, 60 pp. http://hdl.handle.net/10790/3536
  96. Marrack, L. and P. O’Grady, 2014: Predicting Impacts of Sea Level Rise for Cultural and Natural Resources in Five National Park Units on the Island of Hawai’i. Technical report, 188. University of Hawaii at Manoa, Pacific Cooperative Studies Unit, Honolulu, HI, 40 pp. http://hdl.handle.net/10125/34111
  97. Sproat, D.K., 2016: An Indigenous people’s right to environmental self-determination: Native Hawaiians and the struggle against climate change devastation. Stanford Environmental Law Journal, 35 (2). https://law.stanford.edu/publications/an-indigenous-peoples-right-to-environmental-self-determination-native-hawaiians-and-the-struggle-against-climate-change-devastation/
  98. Storlazzi, C.D., S.B. Gingerich, A. van Dongeren, O.M. Cheriton, P.W. Swarzenski, E. Quataert, C.I. Voss, D.W. Field, H. Annamalai, G.A. Piniak, and R. McCall, 2018: Most atolls will be uninhabitable by the mid-21st century because of sea-level rise exacerbating wave-driven flooding. Science Advances, 4 (4), 9741. https://doi.org/10.1126/sciadv.aap9741
  99. Albrecht, G., G.-M. Sartore, L. Connor, N. Higginbotham, S. Freeman, B. Kelly, H. Stain, A. Tonna, and G. Pollard, 2007: Solastalgia: The distress caused by environmental change. Australasian Psychiatry, 15 (Sup1), S95–S98. https://doi.org/10.1080/10398560701701288
  100. Fox, M.D., A.L. Carter, C.B. Edwards, Y. Takeshita, M.D. Johnson, V. Petrovic, C.G. Amir, E. Sala, S.A. Sandin, and J.E. Smith, 2019: Limited coral mortality following acute thermal stress and widespread bleaching on Palmyra Atoll, central Pacific. Coral Reefs, 38 (4), 701–712. https://doi.org/10.1007/s00338-019-01796-7
  101. Baker, J.D., C.L. Littnan, and D.W. Johnston, 2006: Potential effects of sea level rise on the terrestrial habitats of endangered and endemic megafauna in the Northwestern Hawaiian Islands. Endangered Species Research, 2, 21–30. https://doi.org/10.3354/esr002021
  102. Kikiloi, K. and M. Graves, 2010: Ch. 4. Rebirth of an archipelago: Sustaining a Hawaiian cultural identity for people and homeland. In: Hulili: Multidisplinary Research on Hawaiian Well-Being. University of Hawaiʻi Press, 73–116. https://ulukau.org/ulukau-books/?a=d&d=EBOOK-HULILI2010&l=haw
  103. Frazier, A.G., J.L. Deenik, N.D. Fujii, G.R. Funderburk, T.W. Giambelluca, C.P. Giardina, D.A. Helweg, V.W. Keener, A. Mair, J.J. Marra, S. McDaniel, L.N. Ohye, D.S. Oki, E.W. Parsons, A.M. Strauch, and C. Trauernicht, 2019: Ch. 5. Managing effects of drought in Hawai’i and U.S.-affiliated Pacific Islands. In: Effects of Drought on Forests and Rangelands in the United States: Translating Science Into Management Responses. Vose, J.M., D.L. Peterson, C.H. Luce, and T. Patel-Weynand, Eds. U.S. Department of Agriculture, Forest Service, Washington Office, Washington, DC, 95–121. https://www.fs.usda.gov/research/treesearch/59164
  104. Taylor, S., 2021: The vulnerability of health infrastructure to the impacts of climate change and sea level rise in small island countries in the South Pacific. Health Services Insights, 14, 11786329211020857. https://doi.org/10.1177/11786329211020857
  105. Krzesni, D. and L. Brewington, 2022: Climate Change, Health, and Migration: Profiles of Resilience and Vulnerability in the Marshall Islands. East-West Center, Honolulu, HI, 70 pp. https://www.eastwestcenter.org/publications/climate-change-health-and-migration-profiles-resilience-and-vulnerability-in-the
  106. Masselink, G., R. McCall, E. Beetham, P. Kench, and C. Storlazzi, 2021: Role of future reef growth on morphological response of coral reef islands to sea-level rise. Journal of Geophysical Research: Earth Surface, 126 (2), e2020JF005749. https://doi.org/10.1029/2020jf005749
  107. McLean, R. and P. Kench, 2015: Destruction or persistence of coral atoll islands in the face of 20th and 21st century sea-level rise? WIREs Climate Change, 6 (5), 445–463. https://doi.org/10.1002/wcc.350
  108. Storlazzi, C.D., E.P.L. Elias, and P. Berkowitz, 2015: Many atolls may be uninhabitable within decades due to climate change. Scientific Reports, 5, 14546. https://doi.org/10.1038/srep14546
  109. Lam, V.W.Y., E.H. Allison, J.D. Bell, J. Blythe, W.W.L. Cheung, T.L. Frölicher, M.A. Gasalla, and U.R. Sumaila, 2020: Climate change, tropical fisheries and prospects for sustainable development. Nature Reviews Earth & Environment, 1 (9), 440–454. https://doi.org/10.1038/s43017-020-0071-9
  110. Rudiak-Gould, P., 2014: The influence of science communication on Indigenous climate change perception: Theoretical and practical implications. Human Ecology, 42 (1), 75–86. https://doi.org/10.1007/s10745-013-9605-9
  111. McLeod, E., S. Arora-Jonsson, Y.J. Masuda, M. Bruton-Adams, C.O. Emaurois, B. Gorong, C.J. Hudlow, R. James, H. Kuhlken, B. Masike-Liri, E. Musrasrik-Carl, A. Otzelberger, K. Relang, B.M. Reyuw, B. Sigrah, C. Stinnett, J. Tellei, and L. Whitford, 2018: Raising the voices of Pacific Island women to inform climate adaptation policies. Marine Policy, 93, 178–185. https://doi.org/10.1016/j.marpol.2018.03.011
  112. Colin, P.L., 2018: Ocean warming and the reefs of Palau. Oceanography, 31 (2), 126–135. https://doi.org/10.5670/oceanog.2018.214
  113. Miles, W., Z. Grecni, E.X. Matsutaro, P. Colin, V. Keener, and Y. Golbuu, 2020: Climate Change in Palau: Indicators and Considerations for Key Sectors. East-West Center, Honolulu, HI. https://doi.org/10.5281/zenodo.4124259
  114. Carmona, R., J.P. MacDonald, D.S. Dorough, T.B. Rai, G.A. Sanago, and S. Thorsell, 2022: Recognising the Contributions of Indigenous Peoples in Global Climate Action? An Analysis of the IPCC Report on Impacts, Adaptation and Vulnerability. IWGIA Briefing Paper. International Work Group for Indigenous Affairs, 8 pp. https://www.iwgia.org/en/resources/publications/4621-iwgia-briefing-analysing-recognition-contrubutions-indigenous-peoples-ipcc-report.html
  115. IPCC, 2022: Summary for policymakers. In: Climate Change 2022: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change. Pörtner, H.-O., D.C. Roberts, M. Tignor, E.S. Poloczanska, K. Mintenbeck, A. Alegría, M. Craig, S. Langsdorf, S. Löschke, V. Möller, A. Okem, and B. Rama, Eds. Cambridge University Press, Cambridge, UK and New York, NY, USA, 3–33. https://doi.org/10.1017/9781009325844.001
  116. Farmery, A.K., K. Alexander, K. Anderson, J.L. Blanchard, C.G. Carter, K. Evans, M. Fischer, A. Fleming, S. Frusher, E.A. Fulton, B. Haas, C.K. MacLeod, L. Murray, K.L. Nash, G.T. Pecl, Y. Rousseau, R. Trebilco, I.E. van Putten, S. Mauli, L. Dutra, D. Greeno, J. Kaltavara, R. Watson, and B. Nowak, 2022: Food for all: Designing sustainable and secure future seafood systems. Reviews in Fish Biology and Fisheries, 32 (1), 101–121. https://doi.org/10.1007/s11160-021-09663-x
  117. Iese, V., E. Holland, M. Wairiu, R. Havea, S. Patolo, M. Nishi, T. Hoponoa, R.M. Bourke, A. Dean, and L. Waqainabete, 2018: Facing food security risks: The rise and rise of the sweet potato in the Pacific Islands. Global Food Security, 18, 48–56. https://doi.org/10.1016/j.gfs.2018.07.004
  118. Mausio, K., T. Miura, and N.K. Lincoln, 2020: Cultivation potential projections of breadfruit (Artocarpus altilis) under climate change scenarios using an empirically validated suitability model calibrated in Hawai’i. PLoS ONE, 15 (5), 0228552. https://doi.org/10.1371/journal.pone.0228552
  119. Mcleod, E., M. Bruton-Adams, J. Förster, C. Franco, G. Gaines, B. Gorong, R. James, G. Posing-Kulwaum, M. Tara, and E. Terk, 2019: Lessons from the Pacific Islands—Adapting to climate change by supporting social and ecological resilience. Frontiers in Marine Science, 6, 289. https://doi.org/10.3389/fmars.2019.00289
  120. Donato, D.C., J.B. Kauffman, R.A. Mackenzie, A. Ainsworth, and A.Z. Pfleeger, 2012: Whole-island carbon stocks in the tropical Pacific: Implications for mangrove conservation and upland restoration. Journal of Environmental Management, 97, 89–96. https://doi.org/10.1016/j.jenvman.2011.12.004
  121. Elevitch, C.R., D.N. Mazaroli, and D. Ragone, 2018: Agroforestry standards for regenerative agriculture. Sustainability, 10 (9). https://doi.org/10.3390/su10093337
  122. Melone, A., L.L. Bremer, S.E. Crow, Z. Hastings, K.B. Winter, T. Ticktin, Y.M. Rii, M. Wong, K. Kukea-Shultz, S.J. Watson, and C. Trauernicht, 2021: Assessing baseline carbon stocks for forest transitions: A case study of agroforestry restoration from Hawaiʻi. Agriculture, 11 (3). https://doi.org/10.3390/agriculture11030189
  123. Bolden, I.W., S.K. Seroy, E.A. Roberts, L. Schmeisser, J.Z. Koehn, C.H. Rilometo, E.L. Odango, C. Barros, J.P. Sachs, and T. Klinger, 2018: Climate-related community knowledge networks as a tool to increase learning in the context of environmental change. Climate Risk Management, 21, 1–6. https://doi.org/10.1016/j.crm.2018.04.004
  124. Frungillo, J., K. Hougen, B. Merrick, B. Rice, S. Sprague, E. Trelegan, and T.D. Zimmerman, 2022: An Educator’s Guide to the Meaningful Watershed Educational Experience (MWEE). National Oceanic and Atmospheric Administration, Bay Watershed Education and Training Program. https://www.noaa.gov/office-education/bwet/resources/mwee-guide
  125. HWMO, 2021: Ready, Set, Go! Hawaii: Your Personal Wildland Fire Action Guide. Hawai’i Wildlife Management Organization, 20 pp. https://www.hawaiiwildfire.org/fire-resource-library-blog/rsg-your-personal-wildland-fire-action-guide
  126. Longman, R.J., A.G. Frazier, C.P. Giardina, E.W. Parsons, and S. McDaniel, 2022: The Pacific drought knowledge exchange: A co-production approach to deliver climate resources to user groups. Sustainability, 14 (17). https://doi.org/10.3390/su141710554
  127. USGS, 2021: Pacific Islands Climate Adaptation Science Center (PICASC) K12 Education Hub. U.S. Geological Survey, accessed April 12, 2023. https://picasc-education-usgs.hub.arcgis.com/
  128. Dacks, R., H. McMillen, P. Heimuli, K. Kahaleua, S. Burgess, C.P. Giardina, K. Francisco, and T. Ticktin, 2021: The important role of environmental stewardship groups in supporting human health and well-being. Frontiers in Sustainable Cities, 3, 710355. https://doi.org/10.3389/frsc.2021.710355
  129. Qina‘au, J., 2016: BOE Policy E-3: Nā Hopena A‘o (HĀ). McREL International, Honolulu, HI. https://www.hawaiipublicschools.org/doe%20forms/ha-article-july2016.pdf
  130. UNDRR, 2016: UNISDR Annual Report 2015. United Nations Office for Disaster Risk Reduction, Geneva, Switzerland, 75 pp. https://www.undrr.org/publication/unisdr-annual-report-2015
  131. HGG, 2022: Aloha+ Challenge: 2021 Annual Sustainability Scorecard. Hawaii Green Growth. https://alohachallenge.hawaii.gov/pages/2021-annual-sustainability-scorecard
  132. Guam Green Growth, 2021: G3 Action Framework. University of Guam and Office of the Governor of Guam, Mangilao, Guam. https://guamgreengrowth.org/g3-action-framework/
  133. Federated States of Micronesia, 2004: Strategic Development Plan 2004–2023. Federated States of Micronesia, Department of Environment, Climate Change, and Emergency Management. https://fsm-data.sprep.org/resource/strategic-development-plan-2004-2023
  134. Gombos, M., 2020: Micronesia Challenge Evaluation: A Stakeholder-Based Review of a Pioneering Regional Conservation Initiative. Sea Change Consulting. http://www.ourmicronesia.org/strengthening-and-enabling-the-micronesia-challenge-2030.html
  135. Gingerich, S.B., C.I. Voss, and A.G. Johnson, 2017: Seawater-flooding events and impact on freshwater lenses of low-lying islands: Controlling factors, basic management and mitigation. Journal of Hydrology, 551, 676688. https://doi.org/10.1016/j.jhydrol.2017.03.001
  136. Oberle, F.K.J., P.W. Swarzenski, and C.D. Storlazzi, 2017: Atoll groundwater movement and its response to climatic and sea-level fluctuations. Water, 9 (9), 650. https://doi.org/10.3390/w9090650
  137. Clilverd, H.M., Y.P. Tsang, D.M. Infante, A.J. Lynch, and A.M. Strauch, 2019: Long-term streamflow trends in Hawai’i and implications for native stream fauna. Hydrological Processes, 33 (5), 699–719. https://doi.org/10.1002/hyp.13356
  138. Bierque, E., R. Thibeaux, D. Girault, M.-E. Soupé-Gilbert, and C. Goarant, 2020: A systematic review of Leptospira in water and soil environments. PLoS ONE, 15 (1), e0227055. https://doi.org/10.1371/journal.pone.0227055
  139. Economy, L.M., T.N. Wiegner, A.M. Strauch, J.D. Awaya, and T. Gerken, 2019: Rainfall and streamflow effects on estuarine Staphylococcus aureus and fecal indicator bacteria concentrations. Journal of Environmental Quality, 48 (6), 1711–1721. https://doi.org/10.2134/jeq2019.05.0196
  140. Strauch, A.M., R.A. MacKenzie, G.L. Bruland, R. Tingley III, and C.P. Giardina, 2014: Climate change and land use drivers of fecal bacteria in tropical Hawaiian rivers. Journal of Environmental Quality, 43 (4), 1475–1483. https://doi.org/10.2134/jeq2014.01.0025
  141. Strauch, A.M., R.A. MacKenzie, C.P. Giardina, and G.L. Bruland, 2018: Influence of declining mean annual rainfall on the behavior and yield of sediment and particulate organic carbon from tropical watersheds. Geomorphology, 306, 28–39. https://doi.org/10.1016/j.geomorph.2017.12.030
  142. Brewington, L., V. Keener, and A. Mair, 2019: Simulating land cover change impacts on groundwater recharge under selected climate projections, Maui, Hawaiʻi. Remote Sensing, 11 (24), 3048. https://doi.org/10.3390/rs11243048
  143. Hejazian, M., J.J. Gurdak, P. Swarzenski, K.O. Odigie, and C.D. Storlazzi, 2017: Land-use change and managed aquifer recharge effects on the hydrogeochemistry of two contrasting atoll island aquifers, Roi-Namur Island, Republic of the Marshall Islands. Applied Geochemistry, 80, 58–71. https://doi.org/10.1016/j.apgeochem.2017.03.006
  144. Ghazal, K.A., O.T. Leta, A.I. El-Kadi, and H. Dulai, 2019: Assessment of wetland restoration and climate change impacts on water balance components of the Heeia coastal wetland in Hawaii. Hydrology, 6 (2), 37. https://doi.org/10.3390/hydrology6020037
  145. Leta, O.T., A.I. El-Kadi, and H. Dulai, 2017: Implications of climate change on water budgets and reservoir water harvesting of Nuuanu area watersheds, Oahu, Hawaii. Journal of Water Resources Planning and Management, 143 (11), 05017013. https://doi.org/10.1061/(asce)wr.1943-5452.0000839
  146. Leta, O.T., A.I. El-Kadi, and H. Dulai, 2018: Impact of climate change on daily streamflow and its extreme values in Pacific Island watersheds. Sustainability, 10 (6), 2057. https://doi.org/10.3390/su10062057
  147. Mair, A., A.G. Johnson, K. Rotzoll, and D.S. Oki, 2019: Estimated Groundwater Recharge from a Water-Budget Model Incorporating Selected Climate Projections, Island of Maui, Hawai’i. Scientific Investigations Report 2019–5064. U.S. Geological Survey, 46 pp. https://doi.org/10.3133/sir20195064
  148. Strauch, A.M., C.P. Giardina, R.A. MacKenzie, C. Heider, T.W. Giambelluca, E. Salminen, and G.L. Bruland, 2017: Modeled effects of climate change and plant invasion on watershed function across a steep tropical rainfall gradient. Ecosystems, 20 (3), 583–600. https://doi.org/10.1007/s10021-016-0038-3/figures/7
  149. O’Connor, C.F., P.-S. Chu, P.-C. Hsu, and K. Kodama, 2015: Variability of Hawaiian winter rainfall during La Niña events since 1956. Journal of Climate, 28 (19), 7809–7823. https://doi.org/10.1175/jcli-d-14-00638.1
  150. Stevens, L.E., R. Frankson, K.E. Kunkel, P.-S. Chu, and W. Sweet, 2022: Hawai'i State Climate Summary 2022. NOAA Technical Report NESDIS 150-HI. National Oceanic and Atmospheric Administration, National Environmental Satellite, Data, and Information Service, Silver Spring, MD, 5 pp. https://statesummaries.ncics.org/chapter/hi/
  151. Felton, D., 2021: Risks of Sea Level Rise and Increased Flooding on Known Chemical Contamination in Hawaii. Hawaii State Department of Health, Honolulu, HI. https://health.hawaii.gov/heer/files/2021/06/Climate-Change-and-Chemical-Contamination-memo-updated-June-2021.pdf
  152. Denton, G.R.W., C.A. Emborski, N.C. Habana, and J.A. Starmer, 2014: Influence of urban runoff, inappropriate waste disposal practices and World War II on the heavy metal status of sediments in the southern half of Saipan Lagoon, Saipan, CNMI. Marine Pollution Bulletin, 81 (1), 276–281. https://doi.org/10.1016/j.marpolbul.2014.01.014
  153. Nakama, R.K., J.N. Mitchell, and D.S. Oki, 2022: December 23, 2021, Red Hill Synoptic Groundwater-Level Survey, Hālawa Area, O‘ahu, Hawai‘i. USGS Open-File Report 2022-1018. U.S. Geological Survey, Reston, VA, 10 pp. https://doi.org/10.3133/ofr20221018
  154. Jarsjö, J., Y. Andersson-Sköld, M. Fröberg, J. Pietroń, R. Borgström, Å. Löv, and D.B. Kleja, 2020: Projecting impacts of climate change on metal mobilization at contaminated sites: Controls by the groundwater level. Science of The Total Environment, 712, 135560. https://doi.org/10.1016/j.scitotenv.2019.135560
  155. Kibria, G., D. Nugegoda, G. Rose, and A.K.Y. Haroon, 2021: Climate change impacts on pollutants mobilization and interactive effects of climate change and pollutants on toxicity and bioaccumulation of pollutants in estuarine and marine biota and linkage to seafood security. Marine Pollution Bulletin, 167, 112364. https://doi.org/10.1016/j.marpolbul.2021.112364
  156. Alsumaiei, A.A. and R.T. Bailey, 2018: Quantifying threats to groundwater resources in the Republic of Maldives Part II: Recovery from tsunami marine overwash events. Hydrological Processes, 32 (9), 1154–1165. https://doi.org/10.1002/hyp.11473
  157. Babu, R., N. Park, and B. Nam, 2020: Regional and well-scale indicators for assessing the sustainability of small island fresh groundwater lenses under future climate conditions. Environmental Earth Sciences, 79 (1), 47. https://doi.org/10.1007/s12665-019-8773-3
  158. Lassiter, A., 2021: Rising seas, changing salt lines, and drinking water salinization. Current Opinion in Environmental Sustainability, 50, 208–214. https://doi.org/10.1016/j.cosust.2021.04.009
  159. Post, V.E.A., A.L. Bosserelle, S.C. Galvis, P.J. Sinclair, and A.D. Werner, 2018: On the resilience of small-island freshwater lenses: Evidence of the long-term impacts of groundwater abstraction on Bonriki Island, Kiribati. Journal of Hydrology, 564, 133–148. https://doi.org/10.1016/j.jhydrol.2018.06.015
  160. Yang, J., H. Zhang, X. Yu, T. Graf, and H.A. Michael, 2018: Impact of hydrogeological factors on groundwater salinization due to ocean-surge inundation. Advances in Water Resources, 111, 423–434. https://doi.org/10.1016/j.advwatres.2017.11.017
  161. Povak, N.A., C.P. Giardina, P.F. Hessburg, K.M. Reynolds, R.B. Salter, C. Heider, E. Salminen, and R. MacKenzie, 2020: A decision support tool for the conservation of tropical forest and nearshore environments on Babeldaob Island, Palau. Forest Ecology and Management, 476, 118480. https://doi.org/10.1016/j.foreco.2020.118480
  162. DeMartini, E., P. Jokiel, J. Beets, Y. Stender, C. Storlazzi, D. Minton, and E. Conklin, 2013: Terrigenous sediment impact on coral recruitment and growth affects the use of coral habitat by recruit parrotfishes (F. Scaridae). Journal of Coastal Conservation, 17 (3), 417–429. https://doi.org/10.1007/s11852-013-0247-2
  163. Fong, C.R., C.J. Gaynus, and R.C. Carpenter, 2020: Extreme rainfall events pulse substantial nutrients and sediments from terrestrial to nearshore coastal communities: A case study from French Polynesia. Scientific Reports, 10 (1), 2955. https://doi.org/10.1038/s41598-020-59807-5
  164. Rodysill, J.R., J.M. Russell, M. Vuille, S. Dee, B. Lunghino, and S. Bijaksana, 2019: La Niña-driven flooding in the Indo-Pacific warm pool during the past millennium. Quaternary Science Reviews, 225, 106020. https://doi.org/10.1016/j.quascirev.2019.106020
  165. Andrew, N.L., E.H. Allison, T. Brewer, J. Connell, H. Eriksson, J.G. Eurich, A. Farmery, J.A. Gephart, C.D. Golden, M. Herrero, K. Mapusua, K.L. Seto, M.K. Sharp, P. Thornton, A.M. Thow, and J. Tutuo, 2022: Continuity and change in the contemporary Pacific food system. Global Food Security, 32, 100608. https://doi.org/10.1016/j.gfs.2021.100608
  166. Davis, K.F., S. Downs, and J.A. Gephart, 2021: Towards food supply chain resilience to environmental shocks. Nature Food, 2 (1), 54–65. https://doi.org/10.1038/s43016-020-00196-3
  167. Dyer, J., 2017: Ch. 12. Adapting climate change projections to Pacific maritime supply chains. In: Climate Change Adaptation in Pacific Countries: Fostering Resilience and Improving the Quality of Life. Leal Filho, W., Ed. Springer, Cham, Switzerland, 199–223. https://doi.org/10.1007/978-3-319-50094-2_12
  168. Friel, S., A. Schram, and B. Townsend, 2020: The nexus between international trade, food systems, malnutrition and climate change. Nature Food, 1 (1), 51–58. https://doi.org/10.1038/s43016-019-0014-0
  169. Tigchelaar, M., W.W.L. Cheung, E.Y. Mohammed, M.J. Phillips, H.J. Payne, E.R. Selig, C.C.C. Wabnitz, M.A. Oyinlola, T.L. Frölicher, J.A. Gephart, C.D. Golden, E.H. Allison, A. Bennett, L. Cao, J. Fanzo, B.S. Halpern, V.W.Y. Lam, F. Micheli, R.L. Naylor, U.R. Sumaila, A. Tagliabue, and M. Troell, 2021: Compound climate risks threaten aquatic food system benefits. Nature Food, 2 (9), 673–682. https://doi.org/10.1038/s43016-021-00368-9
  170. Allen, M.G., 2015: Framing food security in the Pacific Islands: Empirical evidence from an island in the Western Pacific. Regional Environmental Change, 15 (7), 1341–1353. https://doi.org/10.1007/s10113-014-0734-5
  171. Campbell, J., 2015: Development, global change and traditional food security in Pacific Island countries. Regional Environmental Change, 15, 1313–1324. https://doi.org/10.1007/s10113-014-0697-6
  172. Charlton, K.E., J. Russell, E. Gorman, Q. Hanich, A. Delisle, B. Campbell, and J. Bell, 2016: Fish, food security and health in Pacific Island countries and territories: A systematic literature review. BMC Public Health, 16 (1), 285. https://doi.org/10.1186/s12889-016-2953-9
  173. Connell, J., 2020: Ch. 4. Lost roots? Fading food security in Micronesia. In: Food Security in Small Island States. Connell, J. and K. Lowitt, Eds. Springer, Singapore, 57–76. https://doi.org/10.1007/978-981-13-8256-7_4
  174. Perroy, R.L., J. Melrose, and S. Cares, 2016: The evolving agricultural landscape of post-plantation Hawai‘i. Applied Geography, 76, 154–162. https://doi.org/10.1016/j.apgeog.2016.09.018
  175. Farrell, P., A.M. Thow, J.T. Wate, N. Nonga, P. Vatucawaqa, T. Brewer, M.K. Sharp, A. Farmery, H. Trevena, E. Reeve, H. Eriksson, I. Gonzalez, G. Mulcahy, J.G. Eurich, and N.L. Andrew, 2020: COVID-19 and Pacific food system resilience: Opportunities to build a robust response. Food Security, 12 (4), 783–791. https://doi.org/10.1007/s12571-020-01087-y
  176. Kim, K. and L. Bui, 2019: Learning from Hurricane Maria: Island ports and supply chain resilience. International Journal of Disaster Risk Reduction, 39, 101244. https://doi.org/10.1016/j.ijdrr.2019.101244
  177. Eddy, T.D., V.W.Y. Lam, G. Reygondeau, A.M. Cisneros-Montemayor, K. Greer, M.L.D. Palomares, J.F. Bruno, Y. Ota, and W.W.L. Cheung, 2021: Global decline in capacity of coral reefs to provide ecosystem services. One Earth, 4 (9), 1278–1285. https://doi.org/10.1016/j.oneear.2021.08.016
  178. Gillett, R., 2016: Fisheries in the Economies of Pacific Island Countries and Territories, 2nd ed. Pacific Community, Noumea, New Caledonia. https://www.spc.int/sites/default/files/wordpresscontent/wp-content/uploads/2016/11/Gillett_16_Benefish-fisheries-in-economies-of-pacific-countries.pdf
  179. Munday, P.L., G.P. Jones, M.S. Pratchett, and A.J. Williams, 2008: Climate change and the future for coral reef fishes. Fish and Fisheries, 9 (3), 261–285. https://doi.org/10.1111/j.1467-2979.2008.00281.x
  180. Pippard, H., G.M. Ralph, M.S. Harvey, K.E. Carpenter, J.R. Buchanan, D.W. Greenfield, H.D. Harwell, H.K. Larson, A. Lawrence, C. Linardich, K. Matsuura, H. Motomura, T.A. Munroe, R.F. Myers, B.C. Russell, W.F. Smith-Vaniz, J.-C. Vié, R.R. Thaman, and J.T. Williams, 2017: The Conservation Status of Marine Biodiversity of the Pacific Islands of Oceania. IUCN International Union for Conservation of Nature. https://doi.org/10.2305/iucn.ch.2017.04.en
  181. Bell, J.D., V. Allain, E.H. Allison, S. Andréfouët, N.L. Andrew, M.J. Batty, M. Blanc, J.M. Dambacher, J. Hampton, Q. Hanich, S. Harley, A. Lorrain, M. McCoy, N. McTurk, S. Nicol, G. Pilling, D. Point, M.K. Sharp, P. Vivili, and P. Williams, 2015: Diversifying the use of tuna to improve food security and public health in Pacific Island countries and territories. Marine Policy, 51, 584–591. https://doi.org/10.1016/j.marpol.2014.10.005
  182. Maire, E., N.A.J. Graham, M.A. MacNeil, V.W.Y. Lam, J.P.W. Robinson, W.W.L. Cheung, and C.C. Hicks, 2021: Micronutrient supply from global marine fisheries under climate change and overfishing. Current Biology, 31 (18), 4132–4138. https://doi.org/10.1016/j.cub.2021.06.067
  183. Bell, J.D., M. Kronen, A. Vunisea, W.J. Nash, G. Keeble, A. Demmke, S. Pontifex, and S. Andréfouët, 2009: Planning the use of fish for food security in the Pacific. Marine Policy, 33 (1), 64–76. https://doi.org/10.1016/j.marpol.2008.04.002
  184. Grafeld, S., K.L.L. Oleson, L. Teneva, and J.N. Kittinger, 2017: Follow that fish: Uncovering the hidden blue economy in coral reef fisheries. PLoS ONE, 12 (8), e0182104. https://doi.org/10.1371/journal.pone.0182104
  185. McCoy, K.S., I.D. Williams, A.M. Friedlander, H. Ma, L. Teneva, and J.N. Kittinger, 2018: Estimating nearshore coral reef-associated fisheries production from the main Hawaiian Islands. PLoS ONE, 13 (4), e0195840. https://doi.org/10.1371/journal.pone.0195840
  186. Teneva, L.T., E. Schemmel, and J.N. Kittinger, 2018: State of the plate: Assessing present and future contribution of fisheries and aquaculture to Hawai‘i’s food security. Marine Policy, 94, 28–38. https://doi.org/10.1016/j.marpol.2018.04.025
  187. Hanich, Q., C.C.C. Wabnitz, Y. Ota, M. Amos, C. Donato-Hunt, and A. Hunt, 2018: Small-scale fisheries under climate change in the Pacific Islands region. Marine Policy, 88, 279–284. https://doi.org/10.1016/j.marpol.2017.11.011
  188. Galappaththi, E.K., S.T. Ichien, A.A. Hyman, C.J. Aubrac, and J.D. Ford, 2020: Climate change adaptation in aquaculture. Reviews in Aquaculture, 12 (4), 2160–2176. https://doi.org/10.1111/raq.12427
  189. Oyinlola, M.A., G. Reygondeau, C.C.C. Wabnitz, and W.W.L. Cheung, 2020: Projecting global mariculture diversity under climate change. Global Change Biology, 26 (4), 2134–2148. https://doi.org/10.1111/gcb.14974
  190. Bell, J. and M. Taylor, 2015: Building Climate-Resilient Food Systems for Pacific Islands. Program Report 2015-15. WorldFish, Penang, Malaysia. https://hdl.handle.net/20.500.12348/214
  191. Bell, J., M. Taylor, M. Amos, and N. Andrew, 2016: Climate Change and Pacific Island Food Systems: The Future of Food, Farming and Fishing in the Pacific Islands under a Changing Climate. University of Wollongong, Australia. https://ro.uow.edu.au/lhapapers/3271/
  192. Golden, C.D., E.H. Allison, W.W.L. Cheung, M.M. Dey, B.S. Halpern, D.J. McCauley, M. Smith, B. Vaitla, D. Zeller, and S.S. Myers, 2016: Nutrition: Fall in fish catch threatens human health. Nature, 534 (7607), 317–320. https://doi.org/10.1038/534317a
  193. Ann Singeo (Author), March 15, 2022: Oral communication with Ngarchelong, Palau fishermen, Tino Kloulechad.
  194. Akutagawa, M., H. Williams, S. Kamakaʻala, D.-R. Gibson, M. Kaʻaihue, K. King-Hinds, O. Manglona, K. Nakoa, K. Rawlins-Fernandez, K. Rivera, L.R. Kaʻaekuahiwi, T. Stevenson, and L. Yang, 2016: Traditional & Customary Practices Report for Manaʻe, Molokaʻi: Traditional Subsistence Uses, Mālama Practices and Recommendations, and Native Hawaiian Rights Protections of Kamaʻāina Families of Manaʻe Moku, East Molokaʻi, Hawaiʻi. Office of Hawaiian Affairs. https://doi.org/10.13140/rg.2.1.2697.5125
  195. Sterling, E.J., C. Filardi, A. Toomey, A. Sigouin, E. Betley, N. Gazit, J. Newell, S. Albert, D. Alvira, N. Bergamini, M. Blair, D. Boseto, K. Burrows, N. Bynum, S. Caillon, J.E. Caselle, J. Claudet, G. Cullman, R. Dacks, P.B. Eyzaguirre, S. Gray, J. Herrera, P. Kenilorea, K. Kinney, N. Kurashima, S. Macey, C. Malone, S. Mauli, J. McCarter, H. McMillen, P.a. Pascua, P. Pikacha, A.L. Porzecanski, P. de Robert, M. Salpeteur, M. Sirikolo, M.H. Stege, K. Stege, T. Ticktin, R. Vave, A. Wali, P. West, K.B. Winter, and S.D. Jupiter, 2017: Biocultural approaches to well-being and sustainability indicators across scales. Nature Ecology & Evolution, 1 (12), 1798–1806. https://doi.org/10.1038/s41559-017-0349-6
  196. Iese, V., S. Halavatau, A.D.R. N’Yeurt, M. Wairiu, E. Holland, A. Dean, F. Veisa, S. Patolo, R. Havea, S. Bosenaqali, and O. Navunicagi, 2020: Ch. 9. Agriculture under a changing climate. In: Climate Change and Impacts in the Pacific. Kumar, L., Ed. Springer, Cham, Switzerland, 323–357. https://doi.org/10.1007/978-3-030-32878-8_9
  197. Rosegrant, M.W., R.A. Valmonte-Santos, T. Thomas, L. You, and C.A. Chiang, 2015: Climate Change, Food Security, and Socioeconomic Livelihood in Pacific Islands. Asian Development Bank and International Food Policy Research Institute. https://www.adb.org/publications/climate-change-food-security-socioeconomic-livelihood-pacific
  198. Palanivel, H. and S. Shah, 2021: Unlocking the inherent potential of plant genetic resources: Food security and climate adaptation strategy in Fiji and the Pacific. Environment, Development and Sustainability, 23 (10), 14264–14323. https://doi.org/10.1007/s10668-021-01273-8
  199. Golden, C.D., J.Z. Koehn, A. Shepon, S. Passarelli, C.M. Free, D.F. Viana, H. Matthey, J.G. Eurich, J.A. Gephart, E. Fluet-Chouinard, E.A. Nyboer, A.J. Lynch, M. Kjellevold, S. Bromage, P. Charlebois, M. Barange, S. Vannuccini, L. Cao, K.M. Kleisner, E.B. Rimm, G. Danaei, C. DeSisto, H. Kelahan, K.J. Fiorella, D.C. Little, E.H. Allison, J. Fanzo, and S.H. Thilsted, 2021: Aquatic foods to nourish nations. Nature, 598 (7880), 315–320. https://doi.org/10.1038/s41586-021-03917-1
  200. MacFarland, K., C. Elevitch, J.B. Friday, K. Friday, F.K. Lake, and D. Zamora, 2017: Ch. 5. Human dimensions of agroforestry systems. In: Agroforestry: Enhancing Resiliency in U.S. Agricultural Landscapes Under Changing Conditions. Schoeneberger, M.M., G. Bentrup, and T. Patel-Weynand, Eds. U.S. Department of Agriculture, Forest Service, Washington, DC, 73–90. https://www.fs.usda.gov/research/treesearch/55790
  201. McMillen, H.L., T. Ticktin, A. Friedlander, S.D. Jupiter, R. Thaman, J. Campbell, J. Veitayaki, T. Giambelluca, S. Nihmei, E. Rupeni, L. Apis-Overhoff, W. Aalbersberg, and D.F. Orcherton, 2014: Small islands, valuable insights: Systems of customary resource use and resilience to climate change in the Pacific. Ecology and Society, 19 (4). https://doi.org/10.5751/es-06937-190444
  202. Bremer, L.L., K. Falinski, C. Ching, C.A. Wada, K.M. Burnett, K. Kukea-Shultz, N. Reppun, G. Chun, K.L.L. Oleson, and T. Ticktin, 2018: Biocultural restoration of traditional agriculture: Cultural, environmental, and economic outcomes of Lo‘i Kalo restoration in He‘eia, O‘ahu. Sustainability, 10 (12), 4502. https://doi.org/10.3390/su10124502
  203. Winter, K.B., Y.M. Rii, F.A.W.L. Reppun, K.D. Hintzen, R.A. Alegado, B.W. Bowen, L.L. Bremer, M. Coffman, J.L. Deenik, M.J. Donahue, K.A. Falinski, K. Frank, E.C. Franklin, N. Kurashima, N.K. Lincoln, E.M.P. Madin, M.A. McManus, C.E. Nelson, R. Okano, A. Olegario, P. Pascua, K.L.L. Oleson, M.R. Price, M.A.J. Rivera, K.S. Rodgers, T. Ticktin, C.L. Sabine, C.M. Smith, A. Hewett, R. Kaluhiwa, M. Cypher, B. Thomas, J.-A. Leong, K. Kekuewa, J. Tanimoto, K. Kukea-Shultz, A.H. Kawelo, K. Kotubetey, B.J. Neilson, T.S. Lee, and R.J. Toonen, 2020: Collaborative research to inform adaptive comanagement: A framework for the Heʻeia National Estuarine Research Reserve. Ecology and Society, 25 (4), 15. https://doi.org/10.5751/es-11895-250415
  204. Fardkhales, S.A. and N. Lincoln, 2021: Food hubs play an essential role in the COVID-19 response in Hawai‘i. Journal of Agriculture, Food Systems, and Community Development, 10 (2), 53–70. https://doi.org/10.5304/jafscd.2021.102.036
  205. Ferguson, C.E., T. Tuxson, S. Mangubhai, S. Jupiter, H. Govan, V. Bonito, S. Alefaio, M. Anjiga, J. Booth, T. Boslogo, D. Boso, A. Brenier, A. Caginitoba, A. Ciriyawa, J.B. Fahai’ono, M. Fox, A. George, H. Eriksson, A. Hughes, and M. Waide, 2022: Local practices and production confer resilience to rural Pacific food systems during the COVID-19 pandemic. Marine Policy, 137, 104954. https://doi.org/10.1016/j.marpol.2022.104954
  206. Falanruw, M.V.C., R.M. Perkins, and F. Ruegorong, 2019: Ch. 4. Integrating traditional knowledge and geospatial science to address food security and sustaining biodiversity in Yap Islands, Micronesia. In: Societal Dimensions of Environmental Science. CRC Press, 79–116. https://doi.org/10.1201/9781315166827-4
  207. IPIF, 2020: Partners in Science. U.S. Department of Agriculture, Forest Service, Pacific Southwest Research Station, the Institute of Pacific Islands Forestry, and the U.S.-Affiliated Pacific Islands. https://www.climatehubs.usda.gov/sites/default/files/psw_2020_PartnersInScience.pdf
  208. Del Rosario, A.G., N.M. Esguerra, and T. Taro, 2015: Taro Production in Palau. College of Micronesia Land Grant Programs, 92 pp. https://chm.cbd.int/api/v2013/documents/9A9CE38C-FA3A-4CCB-F77D-EB22E815335B/attachments/212244/Taro-Production_final-2015-optimized.pdf
  209. Aluli, N.E. and D.P. McGregor, 2007: 'Aina: Ke Ola O Na Kanaka 'Oiwi Land: The Health of Native Hawaiians. U.S. Department of Health and Human Services, 15 pp. https://www.nlm.nih.gov/exhibition/avoyagetohealth/pdf/LandandHealth.pdf
  210. Redvers, N., Y. Celidwen, C. Schultz, O. Horn, C. Githaiga, M. Vera, M. Perdrisat, L. Mad Plume, D. Kobei, M.C. Kain, A. Poelina, J.N. Rojas, and B.S. Blondin, 2022: The determinants of planetary health: An Indigenous consensus perspective. The Lancet Planetary Health, 6 (2), 156–163. https://doi.org/10.1016/s2542-5196(21)00354-5
  211. World Health Organization, Food and Agriculture Organization of the United Nations, and World Organisation for Animal Health, 2019: Taking a Multisectoral, One Health Approach: A Tripartite Guide to Addressing Zoonotic Diseases in Countries. World Health Organization, 151 pp. https://apps.who.int/iris/handle/10665/325620
  212. PIFS, 2020: Kainaki II Declaration for Urgent Climate Action Now: Securing the Future of Our Blue Pacific. Pacific Islands Forum Secretariat. https://www.forumsec.org/2020/11/11/kainaki/
  213. Ford, J.D., 2012: Indigenous health and climate change. American Journal of Public Health, 102 (7), 1260–1266. https://doi.org/10.2105/ajph.2012.300752
  214. HDC, 2020: ALICE in Hawaii: A Financial Hardship Study, Aloha United Way. Hawai’i Data Collaborative, 2 pp. https://www.auw.org/alice-initiative
  215. Emanuel, K., 2020: Evidence that hurricanes are getting stronger. Proceedings of the National Academy of Sciences of the United States of America, 117 (24), 13194–13195. https://doi.org/10.1073/pnas.2007742117
  216. Kossin, J.P., K.R. Knapp, T.L. Olander, and C.S. Velden, 2020: Global increase in major tropical cyclone exceedance probability over the past four decades. Proceedings of the National Academy of Sciences of the United States of America, 117 (22), 11975–11980. https://doi.org/10.1073/pnas.1920849117
  217. Stanke, C., M. Kerac, C. Prudhomme, J.M. Medlock, and V. Murray, 2013: Health effects of drought: A systematic review of the evidence. PLoS Currents, 5. https://www.ncbi.nlm.nih.gov/pmc/articles/pmc3682759/
  218. Reguero, B.G., C.D. Storlazzi, A.E. Gibbs, J.B. Shope, A.D. Cole, K.A. Cumming, and M.W. Beck, 2021: The value of US coral reefs for flood risk reduction. Nature Sustainability, 4 (8), 688–698. https://doi.org/10.1038/s41893-021-00706-6
  219. Vitousek, S., P.L. Barnard, C.H. Fletcher, N. Frazer, L. Erikson, and C.D. Storlazzi, 2017: Doubling of coastal flooding frequency within decades due to sea-level rise. Scientific Reports, 7 (1), 1399. https://doi.org/10.1038/s41598-017-01362-7
  220. Romanello, M., A. McGushin, C. Di Napoli, P. Drummond, N. Hughes, L. Jamart, H. Kennard, P. Lampard, B. Solano Rodriguez, N. Arnell, S. Ayeb-Karlsson, K. Belesova, W. Cai, D. Campbell-Lendrum, S. Capstick, J. Chambers, L. Chu, L. Ciampi, C. Dalin, N. Dasandi, S. Dasgupta, M. Davies, P. Dominguez-Salas, R. Dubrow, K.L. Ebi, M. Eckelman, P. Ekins, L.E. Escobar, L. Georgeson, D. Grace, H. Graham, S.H. Gunther, S. Hartinger, K. He, C. Heaviside, J. Hess, S.-C. Hsu, S. Jankin, M.P. Jimenez, I. Kelman, G. Kiesewetter, P.L. Kinney, T. Kjellstrom, D. Kniveton, J.K.W. Lee, B. Lemke, Y. Liu, Z. Liu, M. Lott, R. Lowe, J. Martinez-Urtaza, M. Maslin, L. McAllister, C. McMichael, Z. Mi, J. Milner, K. Minor, N. Mohajeri, M. Moradi-Lakeh, K. Morrissey, S. Munzert, K.A. Murray, T. Neville, M. Nilsson, N. Obradovich, M.O. Sewe, T. Oreszczyn, M. Otto, F. Owfi, O. Pearman, D. Pencheon, M. Rabbaniha, E. Robinson, J. Rocklöv, R.N. Salas, J.C. Semenza, J. Sherman, L. Shi, M. Springmann, M. Tabatabaei, J. Taylor, J. Trinanes, J. Shumake-Guillemot, B. Vu, F. Wagner, P. Wilkinson, M. Winning, M. Yglesias, S. Zhang, P. Gong, H. Montgomery, A. Costello, and I. Hamilton, 2021: The 2021 report of the Lancet Countdown on health and climate change: Code red for a healthy future. The Lancet, 398 (10311), 1619–1662. https://doi.org/10.1016/s0140-6736(21)01787-6
  221. WMO, 2021: WMO Atlas of Mortality and Economic Losses From Weather, Climate and Water Extremes (1970–2019). WMO-No. 1267. World Meteorological Organization, Geneva, Switzerland. https://library.wmo.int/index.php?lvl=notice_display&id=21930#.y437p-zmjpq
  222. Kishore, N., D. Marqués, A. Mahmud, M.V. Kiang, I. Rodriguez, A. Fuller, P. Ebner, C. Sorensen, F. Racy, J. Lemery, L. Maas, J. Leaning, R.A. Irizarry, S. Balsari, and C.O. Buckee, 2018: Mortality in Puerto Rico after Hurricane Maria. New England Journal of Medicine, 379 (2), 162–170. https://doi.org/10.1056/nejmsa1803972
  223. Greene, R. and R. Skeele, 2014: Climate Change Vulnerability Assessment for the Island of Saipan, CNMI. Commonwealth of the Northern Mariana Islands Office of the Governor, Division of Coastal Resources Management, Saipan, 102 pp. https://www.doi.gov/sites/doi.gov/files/cnmi-saipan-vulnerability-assessment.pdf
  224. ASCE, 2020: 2019 Hawaii Infrastructure Report Card. American Society Civil Engineers, 65 pp. https://infrastructurereportcard.org/state-item/hawaii/
  225. Bell, J.E., S.C. Herring, L. Jantarasami, C. Adrianopoli, K. Benedict, K. Conlon, V. Escobar, J. Hess, J. Luvall, C.P. Garcia-Pando, D. Quattrochi, J. Runkle, and C.J. Schreck III, 2016: Ch. 4. Impacts of extreme events on human health. In: The Impacts of Climate Change on Human Health in the United States: A Scientific Assessment. U.S. Global Change Research Program, Washington, DC, 99–128. https://doi.org/10.7930/j0bz63zv
  226. Britton, E. and P. Howden-Chapman, 2011: The effect of climate change on children living on Pacific Islands. In: Climate Change and Rural Child Health. Bell, E., B.M. Seidel, and J. Merrick, Eds. Nova Science Publishers, New York. https://www.researchgate.net/publication/330658034_The_effect_of_climate_change_on_children_living_on_pacific_islands
  227. McIver, L., R. Kim, A. Woodward, S. Hales, J. Spickett, D. Katscherian, M. Hashizume, Y. Honda, H. Kim, S. Iddings, J. Naicker, H. Bambrick, A.J. McMichael, and K.L. Ebi, 2016: Health impacts of climate change in Pacific Island countries: A regional assessment of vulnerabilities and adaptation priorities. Environmental Health Perspectives, 124 (11), 1707–1714. https://doi.org/10.1289/ehp.1509756
  228. RMI and UNICEF, 2017: Republic of the Marshall Islands Integrated Child Health and Nutrition Survey 2017, Final Report. Republic of the Marshall Islands and United Nations Children's Fund, Majuro, RMI. https://www.unicef.org/pacificislands/reports/republic-marshall-islands-integrated-child-health-and-nutrition-survey-2017-report
  229. Dendy, J., D. Mesubed, P.L. Colin, C.P. Giardina, S. Cordell, T. Holm, and A. Uowolo, 2022: Dynamics of anthropogenic wildfire on Babeldaob Island (Palau) as revealed by fire history. Fire, 5 (2), 45. https://doi.org/10.3390/fire5020045
  230. Minton, D., 2006: Fire, Erosion, and Sedimentation in the Asan-Piti Watershed and War in the Pacific NHP, Guam. PCSU Technical Report, 150. University of Hawaii at Manoa, Department of Botany, Pacific Cooperative Studies Unit, Honolulu, HI. http://hdl.handle.net/10125/836
  231. Trauernicht, C., 2017: Wildfire in the Western Pacific, PFX Fact Sheet. Pacific Fire Exchange, Joint Fire Science Program. http://www.c4gts.org/wp-content/uploads/2020/05/Wildfire-in-US-Pacific-Pacific-Fire-Exchange-Fact-Sheet_Final.pdf
  232. Fann, N., T. Brennan, P. Dolwick, J.L. Gamble, V. Ilacqua, L. Kolb, C.G. Nolte, T.L. Spero, and L. Ziska, 2016: Ch. 3. Air quality impacts. In: The Impacts of Climate Change on Human Health in the United States: A Scientific Assessment. U.S. Global Change Research Program, Washington, DC, 69–98. https://doi.org/10.7930/j0gq6vp6
  233. McElfish, P.A., A. Chughtai, L.K. Low, R. Garner, and R.S. Purvis, 2020: ‘Just doing the best we can’: Health care providers’ perceptions of barriers to providing care to Marshallese patients in Arkansas. Ethnicity & Health, 25 (7), 1004–1017. https://doi.org/10.1080/13557858.2018.1471670
  234. McElfish, P.A., E. Hallgren, and S. Yamada, 2015: Effect of US health policies on health care access for Marshallese migrants. American Journal of Public Health, 105 (4), 637–643. https://doi.org/10.2105/ajph.2014.302452
  235. Adger, W.N., J. Barnett, K. Brown, N. Marshall, and K. O'Brien, 2013: Cultural dimensions of climate change impacts and adaptation. Nature Climate Change, 3 (2), 112–117. https://doi.org/10.1038/nclimate1666
  236. Rice, S.M. and L.J. McIver, 2016: Climate change and mental health: Rationale for research and intervention planning. Asian Journal of Psychiatry, 20, 1–2. https://doi.org/10.1016/j.ajp.2015.12.011
  237. Tiatia-Seath, J., T. Tupou, and I. Fookes, 2020: Climate change, mental health, and well-being for Pacific peoples: A literature review. The Contemporary Pacific, 32 (2), 399–430. https://doi.org/10.1353/cp.2020.0035
  238. Asugeni, J., D. MacLaren, P.D. Massey, and R. Speare, 2015: Mental health issues from rising sea level in a remote coastal region of the Solomon Islands: Current and future. Australasian Psychiatry, 23 (supp_6), 22–25. https://doi.org/10.1177/1039856215609767
  239. Gibson, K., N. Haslam, and I. Kaplan, 2019: Distressing encounters in the context of climate change: Idioms of distress, determinants, and responses to distress in Tuvalu. Transcultural Psychiatry, 56 (4), 667–696. https://doi.org/10.1177/1363461519847057
  240. OBrien, L.V., H.L. Berry, C. Coleman, and I.C. Hanigan, 2014: Drought as a mental health exposure. Environmental Research, 131, 181–187. https://doi.org/10.1016/j.envres.2014.03.014
  241. Gray, N.A., M. Wolley, A. Liew, and M. Nakayama, 2015: Natural disasters and dialysis care in the Asia-Pacific. Nephrology, 20 (12), 873–880. https://doi.org/10.1111/nep.12522
  242. Speldewinde, P.C., A. Cook, P. Davies, and P. Weinstein, 2009: A relationship between environmental degradation and mental health in rural Western Australia. Health & Place, 15 (3), 880–887. https://doi.org/10.1016/j.healthplace.2009.02.011
  243. Stillman, S., D. McKenzie, and J. Gibson, 2009: Migration and mental health: Evidence from a natural experiment. Journal of Health Economics, 28 (3), 677–687. https://doi.org/10.1016/j.jhealeco.2009.02.007
  244. Mental Health and Addiction Inquiry, 2018: He Ara Oranga: Report of the Government Inquiry into Mental Health and Addiction. New Zealand Government, Government Inquiry into Mental Health and Addiction. https://mentalhealth.inquiry.govt.nz/inquiry-report/he-ara-oranga/
  245. Cao-Lormeau, V., 2016: Tropical islands as new hubs for emerging arboviruses. Emerging Infectious Diseases, 22 (5), 913–915. https://doi.org/10.3201/eid2205.150547
  246. Matthews, R.J., I. Kaluthotage, T.L. Russell, T.B. Knox, P.F. Horwood, and A.T. Craig, 2022: Arboviral disease outbreaks in the Pacific Islands countries and areas, 2014 to 2020: A systematic literature and document review. Pathogens, 11 (1), 74. https://doi.org/10.3390/pathogens11010074
  247. Filho, W.L., S. Scheday, J. Boenecke, A. Gogoi, A. Maharaj, and S. Korovou, 2019: Climate change, health and mosquito-borne diseases: Trends and implications to the Pacific region. International Journal of Environmental Research and Public Health, 16 (24), 5114. https://doi.org/10.3390/ijerph16245114
  248. PIHOA, 2022: PIHOA Executive Director and Board Vice President Meet with the US Department of State at the Our Ocean Conference in Palau. Pacific Island Health Officers' Association. https://www.pihoa.org/pihoa-executive-director-and-board-vice-president-meet-with-the-us-department-of-state-at-the-our-ocean-conference-in-palau/
  249. Kulkarni, M.A., C. Duguay, and K. Ost, 2022: Charting the evidence for climate change impacts on the global spread of malaria and dengue and adaptive responses: A scoping review of reviews. Globalization and Health, 18 (1), 1. https://doi.org/10.1186/s12992-021-00793-2
  250. CAPA Strategies, 2019: Heat Watch Report. CAPA Strategies Heat Watch Program, Honolulu, HI. https://static1.squarespace.com/static/5e3885654a153a6ef84e6c9c/t/5ee82d0676556f740fa0ef0a/1592274200546/community+heat+assessment+preliminary+report-honolulu_dec_2019-lores.pdf
  251. CCH OCCSR, 2019: Oʻahu Community Heat Map. City and County of Honolulu, Office of Climate Change, Sustainability and Resiliency. https://cchnl.maps.arcgis.com/apps/View/index.html?appid=ff1b73d836074cf6b2aca420fffbd930
  252. Vicedo-Cabrera, A.M., N. Scovronick, F. Sera, D. Royé, R. Schneider, A. Tobias, C. Astrom, Y. Guo, Y. Honda, D.M. Hondula, R. Abrutzky, S. Tong, M.d.S.Z.S. Coelho, P.H.N. Saldiva, E. Lavigne, P.M. Correa, N.V. Ortega, H. Kan, S. Osorio, J. Kyselý, A. Urban, H. Orru, E. Indermitte, J.J.K. Jaakkola, N. Ryti, M. Pascal, A. Schneider, K. Katsouyanni, E. Samoli, F. Mayvaneh, A. Entezari, P. Goodman, A. Zeka, P. Michelozzi, F. de’Donato, M. Hashizume, B. Alahmad, M.H. Diaz, C.D.L.C. Valencia, A. Overcenco, D. Houthuijs, C. Ameling, S. Rao, F. Di Ruscio, G. Carrasco-Escobar, X. Seposo, S. Silva, J. Madureira, I.H. Holobaca, S. Fratianni, F. Acquaotta, H. Kim, W. Lee, C. Iniguez, B. Forsberg, M.S. Ragettli, Y.L.L. Guo, B.Y. Chen, S. Li, B. Armstrong, A. Aleman, A. Zanobetti, J. Schwartz, T.N. Dang, D.V. Dung, N. Gillett, A. Haines, M. Mengel, V. Huber, and A. Gasparrini, 2021: The burden of heat-related mortality attributable to recent human-induced climate change. Nature Climate Change, 11 (6), 492–500. https://doi.org/10.1038/s41558-021-01058-x
  253. Choudhary, E., T.H. Chen, C. Martin, S. Vagi, J. Roth, M. Keim, R. Noe, S.E. Ponausuia, S. Lemusu, T. Bayleyegn, and A. Wolkin, 2012: Public health needs assessments of Tutuila Island, American Samoa, after the 2009 tsunami. Disaster Medicine and Public Health Preparedness, 6 (3), 209–216. https://doi.org/10.1001/dmp.2012.40
  254. Ichiho, H.M. and N. Aitaoto, 2013: Assessing the system of services for chronic diseases prevention and control in the US-affiliated Pacific Islands: Introduction and methods. Hawai'i Journal of Medicine & Public Health, 72 (5), 5–9. https://www.ncbi.nlm.nih.gov/pmc/articles/pmc3689456/
  255. Sievert, K., M. Lawrence, A. Naika, and P. Baker, 2019: Processed foods and nutrition transition in the Pacific: Regional trends, patterns and food system drivers. Nutrients, 11 (6), 1328. https://doi.org/10.3390/nu11061328
  256. SPC, 2019: Pacific Community Results Report: 2018. Pacific Community, Noumea, New Caledonia. https://www.spc.int/updates/blog/2019/07/pacific-community-results-report-2018-year-in-review
  257. Novotny, R., M.K. Fialkowski, F. Li, Y. Paulino, D. Vargo, R. Jim, P. Coleman, A. Bersamin, C.R. Nigg, R.T.L. Guerrero, J. Deenik, J.H. Kim, and L.R. Wilkens, 2015: Systematic review of prevalence of young child overweight and obesity in the United States–Affiliated Pacific region compared with the 48 contiguous states: The children’s healthy living program. American Journal of Public Health, 105 (1), 22–35. https://doi.org/10.2105/ajph.2014.302283
  258. Buehler, J., 2020: The storm, the flood, and the future. Ka Pili Kai Kau. https://seagrant.soest.hawaii.edu/the-storm-the-flood-and-the-future/
  259. Leenders, N., P. Holland, and P. Taylor, 2017: Post Disaster Needs Assessment of the 2015-2016 Drought. Republic of the Marshall Islands. https://www.ilo.org/wcmsp5/groups/public/---ed_emp/documents/publication/wcms_553635.pdf
  260. Bryant-Tokalau, J., 2018: Indigenous Pacific Approaches to Climate Change: Pacific Island Countries. Palgrave Studies in Disaster Anthropology. Palgrave Pivot, Cham, Switzerland, 111 pp. https://doi.org/10.1007/978-3-319-78399-4
  261. Fletcher, S.M., J. Thiessen, A. Gero, M. Rumsey, N. Kuruppu, and J. Willetts, 2013: Traditional coping strategies and disaster response: Examples from the South Pacific region. Journal of Environmental and Public Health, 2013. https://doi.org/10.1155/2013/264503
  262. Granderson, A.A., 2017: The role of traditional knowledge in building adaptive capacity for climate change: Perspectives from Vanuatu. Weather, Climate, and Society, 9 (3), 545–561. https://doi.org/10.1175/wcas-d-16-0094.1
  263. Nakamura, N. and Y. Kanemasu, 2020: Traditional knowledge, social capital, and community response to a disaster: Resilience of remote communities in Fiji after a severe climatic event. Regional Environmental Change, 20 (1), 1–14. https://doi.org/10.1007/s10113-020-01613-w
  264. Austin, S.E., R. Biesbroek, L. Berrang-Ford, J.D. Ford, S. Parker, and M.D. Fleury, 2016: Public health adaptation to climate change in OECD countries. International Journal of Environmental Research and Public Health, 13 (9), 889. https://doi.org/10.3390/ijerph13090889
  265. Dannenberg, A.L., H. Frumkin, J.J. Hess, and K.L. Ebi, 2019: Managed retreat as a strategy for climate change adaptation in small communities: Public health implications. Climatic Change, 153 (1), 1–14. https://doi.org/10.1007/s10584-019-02382-0
  266. Gero, A., S. Fletcher, M. Rumsey, J. Thiessen, N. Kuruppu, J. Buchan, J. Daly, and J. Willetts, 2015: Disasters and climate change in the Pacific: Adaptive capacity of humanitarian response organizations. Climate and Development, 7 (1), 35–46. https://doi.org/10.1080/17565529.2014.899888
  267. Kim, R., A. Costello, and D. Campbell-Lendrum, 2015: Climate change and health in Pacific island states. Bulletin of the World Health Organization, 93, 819. https://doi.org/10.2471/blt.15.166199
  268. Newnham, E.A., P.L. Dzidic, E.L.P. Mergelsberg, B. Guragain, E.Y.Y. Chan, Y. Kim, J. Leaning, R. Kayano, M. Wright, L. Kaththiriarachchi, H. Kato, T. Osawa, and L. Gibbs, 2020: The Asia Pacific disaster mental health network: Setting a mental health agenda for the region. International Journal of Environmental Research and Public Health, 17 (17), 6144. https://doi.org/10.3390/ijerph17176144
  269. Anderson, T.R., C.H. Fletcher, M.M. Barbee, B.M. Romine, S. Lemmo, and J.M.S. Delevaux, 2018: Modeling multiple sea level rise stresses reveals up to twice the land at risk compared to strictly passive flooding methods. Scientific Reports, 8 (1), 14484. https://doi.org/10.1038/s41598-018-32658-x
  270. Habel, S., C.H. Fletcher, T.R. Anderson, and P.R. Thompson, 2020: Sea-level rise induced multi-mechanism flooding and contribution to urban infrastructure failure. Scientific Reports, 10 (1), 3796. https://doi.org/10.1038/s41598-020-60762-4
  271. Anderson, T.R., C.H. Fletcher, M.M. Barbee, L.N. Frazer, and B.M. Romine, 2015: Doubling of coastal erosion under rising sea level by mid-century in Hawaii. Natural Hazards, 78 (1), 75–103. https://doi.org/10.1007/s11069-015-1698-6
  272. Quataert, E., C. Storlazzi, A. van Rooijen, O. Cheriton, and A. van Dongeren, 2015: The influence of coral reefs and climate change on wave-driven flooding of tropical coastlines. Geophysical Research Letters, 42 (15), 6407–6415. https://doi.org/10.1002/2015gl064861
  273. Connell, J. and M. Keen, 2020: Ch. 1. Urbanisation at risk: Urban resilience in Pacific Island countries. In: Urbanisation at Risk in the Pacific and Asia. Sanderson, D. and L. Bruce, Eds. Routledge, New York, NY, 3–21. https://doi.org/10.4324/9780429290176
  274. Act 016: Relating to Coastal Zone Management. S.B. NO. 2060, S.D. 2, H.D. 2, State of Hawai’i, September 15, 2020. https://www.capitol.hawaii.gov/session2020/bills/gm1121_.pdf
  275. Ordinance No. 1088: A Bill for an Ordinance to Amend Chapter 8, Kaua’i County Code 1987, as Amended, Relating to the Comprehensive Zoning Ordinance. Bill No. 2813, Draft 1, State of Hawai’i, County of Kaua'i, January 27, 2021. https://www.kauai.gov/files/assets/public/planning-department/documents/ordinance-no.-1088-bill-no.-2813-draft-1.pdf
  276. Ordinance No. 23-3: A Bill for an Ordinance Relating to Shoreline Setbacks. City and County of Honolulu, March 9, 2023. https://hnldoc.ehawaii.gov/hnldoc/document-download?id=16783
  277. Ordinance No. 23-4: A Bill for an Ordinance Relating to the Special Management Area. City and County of Honolulu, March 9, 2023. https://hnldoc.ehawaii.gov/hnldoc/document-download?id=16784
  278. Maui Planning Commission, 2007: MC-12: Shoreline Rules for the Maui Planning Commission. §12-203. County of Maui, State of Hawaii. https://www.mauicounty.gov/documentcenter/view/8412/chpt-203--mpc-shoreline-procedure-rules?bidid=
  279. Maui Planning Commission, 2022: 2022 Updates: Special Management Area and Shoreline Rules. Maui Planning Commission, Maui, HI, 16 pp. https://www.mauicounty.gov/documentcenter/view/133253/frequently-asked-questions---updated-04222022
  280. Act 179: Relating to Real Property Transactions. SB. No. 0474, S.D. 1, H.D. 2, C.D. 1, State of Hawai’i, July 2, 2021. https://www.capitol.hawaii.gov/session2021/bills/gm1307_.pdf
  281. Act 178: Relating to Sea Level Rise Adaptation. H.B. No. 0243, H.D. 1, S.D. 2, C.D. 1, State of Hawai’i, July 2, 2021. https://www.capitol.hawaii.gov/session2021/bills/gm1306_.pdf
  282. Act 015: Relating to Environmental Protection. H.B. No. 2182, H.D. 2, S.D. 2, C.D. 1, State of Hawai’i, June 4, 2018. https://www.capitol.hawaii.gov/sessions/session2018/bills/GM1115_.PDF
  283. Hawai’i Office of Planning, 2019: Assessing the Feasibility and Implications of Managed Retreat Strategies for Vulnerable Coastal Areas in Hawai’i. Office of Planning, Coastal Zone Management Program, Honolulu, HI. https://files.hawaii.gov/dbedt/op/czm/ormp/assessing_the_feasibility_and_implications_of_managed_retreat_strategies_for_vulnerable_coastal_areas_in_hawaii.pdf
  284. Roelvink, F.E., C.D. Storlazzi, A.R. van Dongeren, and S.G. Pearson, 2021: Coral reef restorations can be optimized to reduce coastal flooding hazards. Frontiers in Marine Science, 8, 653945. https://doi.org/10.3389/fmars.2021.653945
  285. Storlazzi, C.D., B.G. Reguero, K.A. Cumming, A.D. Cole, J.B. Shope, Camila Gaido L., T.S. Viehman, B.A. Nickel, and M.W. Beck, 2021: Rigorously Valuing the Potential Coastal Hazard Risk Reduction Provided by Coral Reef Restoration in Florida and Puerto Rico. USGS Open-File Report 2021–1054. U.S. Geological Survey, Reston, VA, 35 pp. https://doi.org/10.3133/ofr20211054
  286. Campbell, C., n.d.: Reefense. U.S. Department of Defense, Defense Advanced Research Projects Agency. https://www.darpa.mil/program/reefense
  287. Senate Concurrent Resolution: Urging the Department of Land and Natural Resources to Examine and Consider Purchasing Reef Insurance to Support Nature-Based Solutions to Protect Hawaii’s Coastlines and Coastal Infrastructure From Natural Disasters. S.C.R. No. 159, S.D. 1, State of Hawai’i, 2021. https://www.capitol.hawaii.gov/sessions/session2021/bills/scr159_sd1_.htm
  288. An Act to Establish a Tumon Bay Insurance Task Force to Explore the Feasibility of Obtaining Parametric Insurance for the Reef and Beach of Tumon Bay and to Further Explore a Public-Private Partnership to Effectuate the Same. Bill No. 372-35, Territory of Guam, Pub. L. No. 35-107, October 19, 2020. https://guamlegislature.com/35th_public_laws.htm
  289. Ferrario, F., M.W. Beck, C.D. Storlazzi, F. Micheli, C.C. Shepard, and L. Airoldi, 2014: The effectiveness of coral reefs for coastal hazard risk reduction and adaptation. Nature Communications, 5 (1), 3794. https://doi.org/10.1038/ncomms4794
  290. Brander, L. and P. van Beukering, 2013: The Total Economic Value of U.S. Coral Reefs: A Review of the Literature. National Oceanic and Atmospheric Administration, Coral Reef Conservation Program, Silver Spring, MD, 23 pp. https://www.coris.noaa.gov/activities/economic_value/
  291. Storlazzi, C.D., B.G. Reguero, A.D. Cole, E. Lowe, J.B. Shope, A.E. Gibbs, B.A. Nickel, R.T. McCall, A.R. van Dongeren, and M.W. Beck, 2019: Rigorously Valuing the Role of U.S. Coral Reefs in Coastal Hazard Risk Reduction. USGS Open-File Report 2019–1027. U.S. Geological Survey, Reston, VA, 42 pp. https://doi.org/10.3133/ofr20191027
  292. Keen, M. and J. Connell, 2019: Regionalism and resilience? Meeting urban challenges in Pacific island states. Urban Policy and Research, 37 (3), 324–337. https://doi.org/10.1080/08111146.2019.1626710
  293. Connell, J. and R.P.C. Brown, 2005: Remittances in the Pacific: An Overview. Asian Development Bank, Philippines. https://www.adb.org/sites/default/files/publication/28799/remittances-pacific.pdf
  294. The World Bank, 2020: Personal Remittances, Received (% of GDP) - Marshall Islands. World Bank Group. https://data.worldbank.org/indicator/bx.trf.pwkr.dt.gd.zs?locations=mh
  295. The World Bank, 2020: Personal Remittances, Received (% of GDP) - Micronesia, Fed. Sts. World Bank Group. https://data.worldbank.org/indicator/bx.trf.pwkr.dt.gd.zs?locations=fm
  296. The World Bank, 2020: Personal Remittances, Received (% of GDP) - Palau. World Bank Group. https://data.worldbank.org/indicator/bx.trf.pwkr.dt.gd.zs?locations=pw
  297. Campbell, J., 2010: Climate change and population movement in Pacific Island countries. In: Climate Change and Migration South Pacific Perspectives. Burson, B., Ed. Institute of Policy Studies, Wellington, New Zealand, 29–50. https://www.researchgate.net/publication/327638277
  298. Campbell, J. and O. Warrick, 2014: Climate Change and Migration Issues in the Pacific. United Nations Economic and Social Commission for Asia and the Pacific, Fiji. https://www.ilo.org/dyn/migpractice/docs/261/pacific.pdf
  299. van der Geest, K., M. Burkett, J. Fitzpatrick, M. Stege, and B. Wheeler, 2020: Climate change, ecosystem services and migration in the Marshall Islands: Are they related? Climatic Change, 161 (1), 109–127. https://doi.org/10.1007/s10584-019-02648-7
  300. ADB, 2013: The Economics of Climate Change in the Pacific. Asian Development Bank, Madaluyong City, Philippines. https://www.adb.org/sites/default/files/publication/31136/economics-climate-change-pacific.pdf
  301. Fouad, M., N. Novta, G. Preston, T. Schneider, and S. Weerathunga, 2021: Unlocking Access to Climate Finance for Pacific Island Countries. Departmental Paper No. 2021/020. International Monetary Fund, Washington, DC, 103 pp. https://www.imf.org/en/publications/departmental-papers-policy-papers/issues/2021/09/23/unlocking-access-to-climate-finance-for-pacific-islands-countries-464709
  302. Bertram, G., 2013: Ch. 27. Pacific Island economies. In: The Pacific Islands. Rapaport, M., Ed. University of Hawaii Press, Honolulu, HI, 325–340. https://doi.org/10.1515/9780824865849-029
  303. Bertram, I.G. and R.F. Watters, 1986: The MIRAB process: Earlier analyses in context. Pacific Viewpoint, 27 (1), 47–59. https://doi.org/10.1111/apv.271003
  304. Wolf, F., W.L. Filho, P. Singh, N. Scherle, D. Reiser, J. Telesford, I.B. Miljković, P.H. Havea, C. Li, D. Surroop, and M. Kovaleva, 2021: Influences of climate change on tourism development in small Pacific island states. Sustainability, 13 (8), 4223. https://doi.org/10.3390/su13084223
  305. The World Bank, 2022: Agriculture, Forestry, and Fishing, Value Added (% of GDP) - Pacific Island Small States. World Bank Group. https://data.worldbank.org/indicator/nv.agr.totl.zs?locations=s2
  306. Freestone, D. and D. Cicek, 2021: Legal Dimensions of Sea Level Rise: Pacific Perspective. World Bank Group, Washington, DC. http://hdl.handle.net/10986/35881
  307. IPCC, 2014: Climate Change 2014: Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Pachauri, R.K. and L.A. Meyer, Eds. Intergovernmental Panel on Climate Change, Geneva, Switzerland, 151 pp. http://ipcc.ch/report/ar5/syr/
  308. Leatherman, S.P., 2018: Coastal erosion and the United States National Flood Insurance Program. Ocean & Coastal Management, 156, 35–42. https://doi.org/10.1016/j.ocecoaman.2017.04.004
  309. Kumar, L., S. Jayasinghe, T. Gopalakrishnan, and P.D. Nunn, 2020: Ch. 1. Climate change and the Pacific Islands. In: Climate Change and Impacts in the Pacific. Kumar, L., Ed. Springer, Cham, Switzerland, 1–31. https://doi.org/10.1007/978-3-030-32878-8_1
  310. USAID, 2021: USAID assists the Federated States of Micronesia and Palau to secure $10.4 million for climate change adaptation. U.S. Agency for International Development, Washington, DC, April 13, 2021. https://www.usaid.gov/news-information/press-releases/apr-13-2021-usaid-assists-federated-states-micronesia-and-palau-climate-change-adaptation
  311. ADB, 2018: ADB Support to Boost Palau's Resilience to Natural Disasters. Asian Development Bank. https://www.adb.org/news/adb-support-boost-palaus-resilience-natural-disasters
  312. Chapman, A., W. Davies, C. Downey, and D. Dookie, 2021: ADB Climate Risk Country Profile: Micronesia. Asian Development Bank. http://hdl.handle.net/11540/13791
  313. ADB, 2022: The Economic Impacts of the End of Compact Grant Assistance in the Freely Associated States. Asian Development Bank. https://pubs.pitiviti.org/adb-fas
  314. Zhang, D. and S. Lawson, 2017: China in Pacific regional politics. The Round Table, 106 (2), 197–206. https://doi.org/10.1080/00358533.2017.1296705
  315. Buhr, B., U. Volz, C. Donovan, G. Kling, Y.C. Lo, V. Murinde, and N. Pullin, 2018: Climate Change and the Cost of Capital in Developing Countries. Imperial College London, SOAS University of London and UN Environment, London and Geneva. https://eprints.soas.ac.uk/26038/
  316. Act 97: Relating to Renewable Standards. H.B. NO. 623, State of Hawai’i, 245–247, June 8, 2015. https://www.capitol.hawaii.gov/sessions/session2015/bills/hb623_cd1_.pdf
  317. An Act to Amend § 8311 of Article 3, Chapter 8, Title 12, Guam Code Annotated, Relative to Raising the Renewable Portfolio Standards of the Guam Power Authority. Bill No. 80-35, Territory of Guam, Pub. L. No. 35-46, October 31, 2019. https://guamlegislature.com/35th_public_laws.htm
  318. Coffman, M., P. Bernstein, M. Schjervheim, S.L. Croix, and S. Hayashida, 2022: Economic and GHG impacts of a US state-level carbon tax: The case of Hawai‘i. Climate Policy, 22 (7), 935–949. https://doi.org/10.1080/14693062.2022.2061405
  319. RMI, 2018: Tile Til Eo—2050 Climate Strategy "Lighting the Way". Republic of the Marshall Islands. https://unfccc.int/documents/182635
  320. Republic of Palau, 2022: Palau Reaffirms Commitment to Generating 100% Renewable Energy by 2032 as President Whipps Signs the Moana Pledge Transpacific Agreement. Republic of Palau, Office of the President, Ngerulmud, Palau. https://www.manapacific.com/wp-content/uploads/2022/04/PR22-09-Moana-Pledge_Mana-Pacific.pdf
  321. McNamara, K.E., R. Clissold, R. Westoby, A.E. Piggott-McKellar, R. Kumar, T. Clarke, F. Namoumou, F. Areki, E. Joseph, O. Warrick, and P.D. Nunn, 2020: An assessment of community-based adaptation initiatives in the Pacific Islands. Nature Climate Change, 10 (7), 628–639. https://doi.org/10.1038/s41558-020-0813-1
  322. Nalau, J., S. Becken, and B. Mackey, 2018: Ecosystem-based adaptation: A review of the constraints. Environmental Science & Policy, 89, 357–364. https://doi.org/10.1016/j.envsci.2018.08.014
  323. Nunn, P.D., A. Kohler, and R. Kumar, 2017: Identifying and assessing evidence for recent shoreline change attributable to uncommonly rapid sea-level rise in Pohnpei, Federated States of Micronesia, northwest Pacific Ocean. Journal of Coastal Conservation, 21 (6), 719–730. https://doi.org/10.1007/s11852-017-0531-7
  324. Harvey, C., 2016: This island is now powered almost entirely by solar energy. The Washington Post, November 24, 2016. https://www.washingtonpost.com/news/energy-environment/wp/2016/11/24/this-island-is-now-powered-almost-entirely-by-solar-energy/
  325. Hawaii State Energy Office, 2020: Hawai‘i’s Energy Facts and Figures. Hawaii State Energy Office. https://energy.hawaii.gov/wp-content/uploads/2020/11/HSEO_FactsAndFigures-2020.pdf
  326. Kauaʻi Island Utility Cooperative, 2022: 2021 Annual Renewable Portfolio Standards Status Report. Hawaii Public Utilities Commission, Honolulu, HI. https://dms.puc.hawaii.gov/dms/DocumentViewer?pid=A1001001A22D01A95234F01510
  327. Sylvia, T., 2019: Kauai was 100% renewably powered for 32 hours over the last month. PV Magazine. https://pv-magazine-usa.com/2019/12/19/in-the-last-month-kauaii-has-been-100-renewably-powered-for-32-hours/
  328. Act 100: Relating to Energy. S.B. NO. 1050, S.D.2, H.D.3, C.D.1, State of Hawai’i, June 8, 2015. https://www.capitol.hawaii.gov/sessions/session2015/bills/gm1200_.pdf
  329. Teruya, L., 2021: Molokai Has an Electricity Problem. This Co-op Wants to Change That. Honolulu Civil Beat. https://www.civilbeat.org/2021/09/molokai-has-an-electricity-problem-this-co-op-wants-to-change-that/
  330. Rubalcaba, J.G., W.C.E.P. Verberk, A.J. Hendriks, B. Saris, and H.A. Woods, 2020: Oxygen limitation may affect the temperature and size dependence of metabolism in aquatic ectotherms. Proceedings of the National Academy of Sciences of the United States of America, 117 (50), 31963–31968. https://doi.org/10.1073/pnas.2003292117
  331. Lotze, H.K., D.P. Tittensor, A. Bryndum-Buchholz, T.D. Eddy, W.W.L. Cheung, E.D. Galbraith, M. Barange, N. Barrier, D. Bianchi, J.L. Blanchard, L. Bopp, M. Büchner, C.M. Bulman, D.A. Carozza, V. Christensen, M. Coll, J.P. Dunne, E.A. Fulton, S. Jennings, and B. Worm, 2019: Global ensemble projections reveal trophic amplification of ocean biomass declines with climate change. Proceedings of the National Academy of Sciences of the United States of America, 116 (26), 12907–12912. https://doi.org/10.1073/pnas.1900194116
  332. Hoegh-Guldberg, O., D. Beal, T. Chaudhry, H. Elhaj, A. Abdullat, P. Etessy, and M. Smits, 2015: Reviving the Oceans Economy: The Case for Action—2015. WWF International, Gland, Switzerland, Geneva, 60 pp. https://www.worldwildlife.org/publications/reviving-the-oceans-economy-the-case-for-action-2015
  333. Moritz, C., J. Vii, W. Lee Long, J. Tamelander, A. Thomassin, and S. Planes, 2018: Status and Trends of Coral Reefs of the Pacific. Global Coral Reef Monitoring Network. https://www.unep.org/resources/report/status-and-trends-coral-reef-pacific
  334. Raymundo, L.J., D. Burdick, W.C. Hoot, R.M. Miller, V. Brown, T. Reynolds, J. Gault, J. Idechong, J. Fifer, and A. Williams, 2019: Successive bleaching events cause mass coral mortality in Guam, Micronesia. Coral Reefs, 38 (4), 677–700. https://doi.org/10.1007/s00338-019-01836-2
  335. Brainard, R.E., T. Oliver, M.J. McPhaden, A. Cohen, R. Venegas, A. Heenan, B. Vargas-Ángel, R. Rotjan, S. Mangubhai, E. Flint, and S.A. Hunter, 2018: Ecological impacts of the 2015/16 El Niño in the central equatorial Pacific. Bulletin of the American Meteorological Society, 99 (1), S21–S26. https://doi.org/10.1175/bams-d-17-0128.1
  336. Hughes, T.P., K.D. Anderson, S.R. Connolly, S.F. Heron, J.T. Kerry, J.M. Lough, A.H. Baird, J.K. Baum, M.L. Berumen, T.C. Bridge, D.C. Claar, C.M. Eakin, J.P. Gilmour, N.A.J. Graham, H. Harrison, J.-P.A. Hobbs, A.S. Hoey, M. Hoogenboom, R.J. Lowe, M.T. McCulloch, J.M. Pandolfi, M. Pratchett, V. Schoepf, G. Torda, and S.K. Wilson, 2018: Spatial and temporal patterns of mass bleaching of corals in the Anthropocene. Science, 359 (6371), 80–83. https://doi.org/10.1126/science.aan8048
  337. Graham, N.A.J., J.P.W. Robinson, S.E. Smith, R. Govinden, G. Gendron, and S.K. Wilson, 2020: Changing role of coral reef marine reserves in a warming climate. Nature Communications, 11 (1), 2000. https://doi.org/10.1038/s41467-020-15863-z
  338. McManus, L.C., D.L. Forrest, E.W. Tekwa, D.E. Schindler, M.A. Colton, M.M. Webster, T.E. Essington, S.R. Palumbi, P.J. Mumby, and M.L. Pinsky, 2021: Evolution and connectivity influence the persistence and recovery of coral reefs under climate change in the Caribbean, Southwest Pacific, and Coral Triangle. Global Change Biology, 27 (18), 4307–4321. https://doi.org/10.1111/gcb.15725
  339. Robinson, J.P.W., S.K. Wilson, S. Jennings, and N.A.J. Graham, 2019: Thermal stress induces persistently altered coral reef fish assemblages. Global Change Biology, 25 (8), 2739–2750. https://doi.org/10.1111/gcb.14704
  340. Jensen, M.P., C.D. Allen, T. Eguchi, I.P. Bell, E.L. LaCasella, W.A. Hilton, C.A.M. Hof, and P.H. Dutton, 2018: Environmental warming and feminization of one of the largest sea turtle populations in the world. Current Biology, 28 (1), 154–159. https://doi.org/10.1016/j.cub.2017.11.057
  341. He, Q. and B.R. Silliman, 2019: Climate change, human impacts, and coastal ecosystems in the Anthropocene. Current Biology, 29 (19), R1021–R1035. https://doi.org/10.1016/j.cub.2019.08.042
  342. Marrack, L., C. Wiggins, J.J. Marra, A. Genz, R. Most, K. Falinski, and E. Conklin, 2021: Assessing the spatial–temporal response of groundwater-fed anchialine ecosystems to sea-level rise for coastal zone management. Aquatic Conservation: Marine and Freshwater Ecosystems, 31 (4), 853–869. https://doi.org/10.1002/aqc.3493
  343. Suárez-Castro, A.F., H.L. Beyer, C.D. Kuempel, S. Linke, P. Borrelli, and O. Hoegh-Guldberg, 2021: Global forest restoration opportunities to foster coral reef conservation. Global Change Biology, 27 (20), 5238–5252. https://doi.org/10.1111/gcb.15811
  344. Allemand, D. and D. Osborn, 2019: Ocean acidification impacts on coral reefs: From sciences to solutions. Regional Studies in Marine Science, 28, 100558. https://doi.org/10.1016/j.rsma.2019.100558
  345. Prouty, N.G., A. Cohen, K.K. Yates, C.D. Storlazzi, P.W. Swarzenski, and D. White, 2017: Vulnerability of coral reefs to bioerosion from land-based source of pollution. Journal of Geophysical Research Oceans, 122 (12), 9319–9331. https://doi.org/10.1002/2017jc013264
  346. Beyer, H.L., E.V. Kennedy, M. Beger, C.A. Chen, J.E. Cinner, E.S. Darling, C.M. Eakin, R.D. Gates, S.F. Heron, N. Knowlton, D.O. Obura, S.R. Palumbi, H.P. Possingham, M. Puotinen, R.K. Runting, W.J. Skirving, M. Spalding, K.A. Wilson, S. Wood, and O. Hoegh-Guldberg, 2018: Risk-sensitive planning for conserving coral reefs under rapid climate change. Conservation Letters, 11 (6), 12587. https://doi.org/10.1111/conl.12587
  347. Twilley, R.R., E. Castañeda-Moya, V.H. Rivera-Monroy, and A. Rovai, 2017: Ch. 5. Productivity and carbon dynamics in mangrove wetlands. In: Mangrove Ecosystems: A Global Biogeographic Perspective. Rivera-Monroy, V.H., S.Y. Lee, E. Kristensen, and R.R. Twilley, Eds. Springer, Cham, Switzerland, 113–162. https://doi.org/10.1007/978-3-319-62206-4_5
  348. Herr, D. and E. Landis, 2016: Coastal Blue Carbon Ecosystems: Opportunities for Nationally Determined Contributions. Policy Brief. International Union for Conservation of Nature and The Nature Conservancy, Gland, Switzerland and Washington, DC. https://www.unep.org/resources/policy-and-strategy/coastal-blue-carbon-ecosystems-opportunities-nationally-determined
  349. Hilmi, N., R. Chami, M.D. Sutherland, J.M. Hall-Spencer, L. Lebleu, M.B. Benitez, and L.A. Levin, 2021: The role of blue carbon in climate change mitigation and carbon stock conservation. Frontiers in Climate, 3, 710546. https://doi.org/10.3389/fclim.2021.710546
  350. Naylor, R.L., K.M. Bonine, K.C. Ewel, and E. Waguk, 2002: Migration, markets, and mangrove resource use on Kosrae, Federated States of Micronesia. AMBIO: A Journal of the Human Environment, 31 (4), 340–350. https://doi.org/10.1579/0044-7447-31.4.340
  351. Engilis Jr., A. and M.B. Naughton, 2004: U.S. Pacific Islands Regional Shorebird Conservation Plan. U.S. Shorebird Conservation Plan. U.S. Department of the Interior, Fish and Wildlife Service, Portland, OR. https://www.shorebirdplan.org/wp-content/uploads/2013/01/USPI1.pdf
  352. Field, M.E., S.A. Cochran, J.B. Logan, and C.D. Storlazzi, 2008: The Coral Reef of South Moloka‘i, Hawai‘i—Portrait of a Sediment-Threatened Fringing Reef. Scientific Investigations Report 2007-5101. U.S. Geological Survey. https://pubs.usgs.gov/sir/2007/5101/
  353. Soper, F.M., R.A. MacKenzie, S. Sharma, T.G. Cole, C.M. Litton, and J.P. Sparks, 2019: Non-native mangroves support carbon storage, sediment carbon burial, and accretion of coastal ecosystems. Global Change Biology, 25 (12), 4315–4326. https://doi.org/10.1111/gcb.14813
  354. Jacobi, J.D. and F.R. Warshauer, 2017: Hawaiian Islands Coastal Vegetation Survey 2013-2015. U.S. Geological Survey. https://doi.org/10.5066/f7tt4pvb
  355. Saintilan, N., N.S. Khan, E. Ashe, J.J. Kelleway, K. Rogers, C.D. Woodroffe, and B.P. Horton, 2020: Thresholds of mangrove survival under rapid sea level rise. Science, 368 (6495), 1118–1121. https://doi.org/10.1126/science.aba2656
  356. Reynolds, M.H., K.N. Courtot, P. Berkowitz, C.D. Storlazzi, J. Moore, and E. Flint, 2015: Will the effects of sea-level rise create ecological traps for Pacific Island seabirds? PLoS ONE, 10 (9), e0136773. https://doi.org/10.1371/journal.pone.0136773
  357. IPCC, 2019: IPCC Special Report on the Ocean and Cryosphere in a Changing Climate. Pörtner, H.-O., D.C. Roberts, V. Masson-Delmotte, P. Zhai, M. Tignor, E. Poloczanska, K. Mintenbeck, A. Alegría, M. Nicolai, A. Okem, J. Petzold, B. Rama, and N.M. Weyer, Eds. Cambridge University Press, Cambridge, UK and New York, NY, USA, 755 pp. https://doi.org/10.1017/9781009157964
  358. Blackburn, T.M., P. Cassey, R.P. Duncan, K.L. Evans, and K.J. Gaston, 2004: Avian extinction and mammalian introductions on oceanic islands. Science, 305 (5692), 1955–1958. https://doi.org/10.1126/science.1101617
  359. Brewington, L., B. Eichelberger, N. Read, E. Parsons, H. Kerkering, C. Martin, W. Miles, J. Idechong, and J. Burgett, 2023: Ch. 5. Pacific Island perspectives on invasive species and climate change. In: Island Ecosystems: Challenges to Sustainability. Walsh, S.J., C.F. Mena, J.R. Stewart, and J.P. Muñoz Pérez, Eds. Springer, Cham, Switzerland, 59–78. https://doi.org/10.1007/978-3-031-28089-4_5
  360. Fernández-Palacios, J.M., H. Kreft, S.D.H. Irl, S. Norder, C. Ah-Peng, P.A.V. Borges, K.C. Burns, L. de Nascimento, J.-Y. Meyer, E. Montes, and D.R. Drake, 2021: Scientists’ warning – The outstanding biodiversity of islands is in peril. Global Ecology and Conservation, 31, e01847. https://doi.org/10.1016/j.gecco.2021.e01847
  361. Leclerc, C., F. Courchamp, and C. Bellard, 2018: Insular threat associations within taxa worldwide. Scientific Reports, 8 (1), 6393. https://doi.org/10.1038/s41598-018-24733-0
  362. Pyšek, P., V. Jarošík, P.E. Hulme, J. Pergl, M. Hejda, U. Schaffner, and M. Vilà, 2012: A global assessment of invasive plant impacts on resident species, communities and ecosystems: The interaction of impact measures, invading species' traits and environment. Global Change Biology, 18 (5), 1725–1737. https://doi.org/10.1111/j.1365-2486.2011.02636.x
  363. Wilcove, D.S., D. Rothstein, J. Dubow, A. Phillips, and E. Losos, 1998: Quantifying threats to imperiled species in the United States: Assessing the relative importance of habitat destruction, alien species, pollution, overexploitation, and disease. BioScience, 48 (8), 607–615. https://doi.org/10.2307/1313420
  364. Barbosa, J.M. and G.P. Asner, 2016: Effects of long-term rainfall decline on the structure and functioning of Hawaiian forests. Environmental Research Letters, 12 (9), 094002. https://doi.org/10.1088/1748-9326/aa7ee4
  365. Madson, A., M. Dimson, L.B. Fortini, K. Kawelo, T. Ticktin, M. Keir, C. Dong, Z. Ma, D.W. Beilman, K. Kay, J.P. Ocón, E. Gallerani, S. Pau, and T.W. Gillespie, 2022: A near four-decade time series shows the Hawaiian Islands have been browning since the 1980s. Environmental Management, 71 (5), 965–980. https://doi.org/10.1007/s00267-022-01749-x
  366. Banko, P.C., R.J. Camp, C. Farmer, K.W. Brinck, D.L. Leonard, and R.M. Stephens, 2013: Response of palila and other subalpine Hawaiian forest bird species to prolonged drought and habitat degradation by feral ungulates. Biological Conservation, 157, 70–77. https://doi.org/10.1016/j.biocon.2012.07.013
  367. Fortini, L., J. Price, J. Jacobi, A. Vorsino, J. Burgett, K. Brinck, S. ‘Ohukani‘ohi‘a Gon III, G. Koob, and E. Paxton, 2013: A Landscape-Based Assessment of Climate Change Vulnerability for All Native Hawaiian Plants. Technical Report HCSU-044. University of Hawai‘i, Hawai‘i Cooperative Studies Unit, Hilo, HI. https://hilo.hawaii.edu/hcsu/documents/TR44_Fortini_plant_vulnerability_assessment.pdf
  368. Barton, K.E., C. Jones, K.F. Edwards, A.B. Shiels, and T. Knight, 2020: Local adaptation constrains drought tolerance in a tropical foundation tree. Journal of Ecology, 108 (4), 1540–1552. https://doi.org/10.1111/1365-2745.13354
  369. Eldon, J., M.R. Bellinger, and D.K. Price, 2019: Hawaiian picture‐winged Drosophila exhibit adaptive population divergence along a narrow climatic gradient on Hawaii Island. Ecology and Evolution, 9 (5), 2436–2448. https://doi.org/10.1002/ece3.4844
  370. Fortini, L.B., P.D. Krushelnycky, D.R. Drake, F. Starr, K. Starr, and C.G. Chimera, 2022: Complex demographic responses to contrasting climate drivers lead to divergent population trends across the range of a threatened alpine plant. Global Ecology and Conservation, 33, 01954. https://doi.org/10.1016/j.gecco.2021.e01954
  371. Westerband, A.C., L. Bialic-Murphy, L.A. Weisenberger, and K.E. Barton, 2020: Intraspecific variation in seedling drought tolerance and associated traits in a critically endangered, endemic Hawaiian shrub. Plant Ecology & Diversity, 13 (2), 159–174. https://doi.org/10.1080/17550874.2020.1730459
  372. Tsang, Y.-P., R.W. Tingley, J. Hsiao, and D.M. Infante, 2019: Identifying high value areas for conservation: Accounting for connections among terrestrial, freshwater, and marine habitats in a tropical island system. Journal for Nature Conservation, 50, 125711. https://doi.org/10.1016/j.jnc.2019.125711
  373. Frauendorf, T.C., R.A. MacKenzie, R.W. Tingley III, D.M. Infante, and R.W. El-Sabaawi, 2020: Using a space-for-time substitution approach to predict the effects of climate change on nutrient cycling in tropical island stream ecosystems. Limnology and Oceanography, 65 (12), 3114–3127. https://doi.org/10.1002/lno.11577
  374. Gagne, R.B. and M.J. Blum, 2016: Parasitism of a native Hawaiian stream fish by an introduced nematode increases with declining precipitation across a natural rainfall gradient. Ecology of Freshwater Fish, 25 (3), 476–486. https://doi.org/10.1111/eff.12228
  375. Tingley III, R.W. 2017: Conserving Streams With Changing Climate: A Multi-Scaled Research Framework to Consider Current and Future Condition of Hawaiian Stream Habitats. Doctor of Philosophy in Fisheries and Wildlife, Michigan State University, 181 pp. https://d.lib.msu.edu/etd/4575
  376. Nugent, A.D., R.J. Longman, C. Trauernicht, M.P. Lucas, H.F. Diaz, and T.W. Giambelluca, 2020: Fire and rain: The legacy of Hurricane Lane in Hawaiʻi. Bulletin of the American Meteorological Society, 101 (6), 954–967. https://doi.org/10.1175/bams-d-19-0104.1
  377. Trauernicht, C., 2019: Vegetation—rainfall interactions reveal how climate variability and climate change alter spatial patterns of wildland fire probability on Big Island, Hawaii. Science of The Total Environment, 650, 459–469. https://doi.org/10.1016/j.scitotenv.2018.08.347
  378. Trauernicht, C., E. Pickett, C.P. Giardina, C.M. Litton, S. Cordell, and A. Beavers, 2015: The contemporary scale and context of wildfire in Hawaiʻi. Pacific Science, 69 (4), 427–444. https://doi.org/10.2984/69.4.1
  379. Aslan, C.E., C.T. Liang, A.B. Shiels, and W. Haines, 2018: Absence of native flower visitors for the endangered Hawaiian mint Stenogyne angustifolia: Impending ecological extinction? Global Ecology and Conservation, 16, e00468. https://doi.org/10.1016/j.gecco.2018.e00468
  380. Fortini, L.B., C.R. Leopold, K.S. Perkins, O.A. Chadwick, S.G. Yelenik, J.D. Jacobi, K. Bishaw, and M. Gregg, 2021: Landscape level effects of invasive plants and animals on water infiltration through Hawaiian tropical forests. Biological Invasions, 23 (7), 2155–2172. https://doi.org/10.1007/s10530-021-02494-8
  381. Ibanez, T. and P.J. Hart, 2020: Spatial patterns of tree recruitment in a montane Hawaiian wet forest after cattle removal and pig population control. Applied Vegetation Science, 23 (2), 197–209. https://doi.org/10.1111/avsc.12478
  382. Strauch, A.M., G.L. Bruland, R.A. MacKenzie, and C.P. Giardina, 2016: Soil and hydrological responses to wild pig (Sus scofa) exclusion from native and strawberry guava (Psidium cattleianum)-invaded tropical montane wet forests. Geoderma, 279, 53–60. https://doi.org/10.1016/j.geoderma.2016.05.021
  383. Yeung, N.W. and K.A. Hayes, 2018: Biodiversity and extinction of Hawaiian land snails: How many are left now and what must we do to conserve them—A reply to Solem (1990). Integrative and Comparative Biology, 58 (6), 1157–1169. https://doi.org/10.1093/icb/icy043
  384. Ainsworth, A. and D.R. Drake, 2020: Classifying Hawaiian plant species along a habitat generalist-specialist continuum: Implications for species conservation under climate change. PLoS ONE, 15 (2), 0228573. https://doi.org/10.1371/journal.pone.0228573
  385. Louppe, V., B. Leroy, A. Herrel, and G. Veron, 2020: The globally invasive small Indian mongoose Urva auropunctata is likely to spread with climate change. Scientific Reports, 10 (1), 7461. https://doi.org/10.1038/s41598-020-64502-6
  386. Sommer, R.M. and R.H. Cowie, 2020: Invasive traits of veronicellid slugs in the Hawaiian Islands and temperature response suggesting possible range shifts under a changing climate. Journal of Molluscan Studies, 86 (2), 147–155. https://doi.org/10.1093/mollus/eyz042
  387. Veazey, L., O. Williams, R. Wade, R. Toonen, and H.L. Spalding, 2019: Present-day distribution and potential spread of the invasive green alga Avrainvillea amadelpha around the main Hawaiian Islands. Frontiers in Marine Science, 6, 402. https://doi.org/10.3389/fmars.2019.00402
  388. Dudley, B.D., R.F. Hughes, G.P. Asner, J.A. Baldwin, Y. Miyazawa, H. Dulai, C. Waters, J. Bishop, N.R. Vaughn, J. Yeh, S. Kettwich, R.A. MacKenzie, R. Ostertag, and T. Giambelluca, 2020: Hydrological effects of tree invasion on a dry coastal Hawaiian ecosystem. Forest Ecology and Management, 458, 117653. https://doi.org/10.1016/j.foreco.2019.117653
  389. Michaud, J., S. Cordell, T.C. Cole, and R. Ostertag, 2015: Drought in an invaded Hawaiian lowland wet forest. Pacific Science, 69 (3), 367–383. https://doi.org/10.2984/69.3.6
  390. Takahashi, M., T.W. Giambelluca, R.G. Mudd, J.K. DeLay, M.A. Nullet, and G.P. Asner, 2011: Rainfall partitioning and cloud water interception in native forest and invaded forest in Hawai'i Volcanoes National Park. Hydrological Processes, 25 (3), 448–464. https://doi.org/10.1002/hyp.7797
  391. van Kleunen, M., W. Dawson, F. Essl, J. Pergl, M. Winter, E. Weber, H. Kreft, P. Weigelt, J. Kartesz, M. Nishino, L.A. Antonova, J.F. Barcelona, F.J. Cabezas, D. Cárdenas, J. Cárdenas-Toro, N. Castaño, E. Chacón, C. Chatelain, A.L. Ebel, E. Figueiredo, N. Fuentes, Q.J. Groom, L. Henderson, Inderjit, A. Kupriyanov, S. Masciadri, J. Meerman, O. Morozova, D. Moser, D.L. Nickrent, A. Patzelt, P.B. Pelser, M.P. Baptiste, M. Poopath, M. Schulze, H. Seebens, W.-s. Shu, J. Thomas, M. Velayos, J.J. Wieringa, and P. Pyšek, 2015: Global exchange and accumulation of non-native plants. Nature, 525 (7567), 100–103. https://doi.org/10.1038/nature14910
  392. Beaury, E.M., J.T. Finn, J.D. Corbin, V. Barr, and B.A. Bradley, 2020: Biotic resistance to invasion is ubiquitous across ecosystems of the United States. Ecology Letters, 23 (3), 476–482. https://doi.org/10.1111/ele.13446
  393. U.S. Department of the Navy, 2015: Regional Biosecurity Plan for Micronesia and Hawaii. Volume I. University of Guam and the Secretariat of the Pacific Community. https://www.doi.gov/sites/doi.gov/files/uploads/pac_regional_biosecurity_plan_for_micronesia_and_hawaii_volume_i.pdf
  394. Finch, D.M., J.L. Butler, J.B. Runyon, C.J. Fettig, F.F. Kilkenny, S. Jose, S.J. Frankel, S.A. Cushman, R.C. Cobb, J.S. Dukes, J.A. Hicke, and S.K. Amelon, 2021: Ch. 4. Effects of climate change on invasive species. In: Invasive Species in Forests and Rangelands of the United States: A Comprehensive Science Synthesis for the United States Forest Sector. Poland, T.M., T. Patel-Weynand, D.M. Finch, C.F. Miniat, D.C. Hayes, and V.M. Lopez, Eds. Springer, Cham, Switzerland, 57–83. https://doi.org/10.1007/978-3-030-45367-1_4
  395. Hellmann, J.J., J.E. Byers, B.G. Bierwagen, and J.S. Dukes, 2008: Five potential consequences of climate change for invasive species. Conservation Biology, 22 (3), 534–543. https://doi.org/10.1111/j.1523-1739.2008.00951.x
  396. Lockwood, J.L., M.F. Hoopes, and M.P. Marchetti, 2013: Invasion Ecology. Wiley-Blackwell, 456 pp. https://www.wiley.com/en-ie/invasion+ecology,+2nd+edition-p-9781444333640
  397. Balzotti, C.S., G.P. Asner, E.D. Adkins, and E.W. Parsons, 2020: Spatial drivers of composition and connectivity across endangered tropical dry forests. Journal of Applied Ecology, 57 (8), 1593–1604. https://doi.org/10.1111/1365-2664.13632
  398. Barbosa, J.M. and G.P. Asner, 2017: Prioritizing landscapes for restoration based on spatial patterns of ecosystem controls and plant–plant interactions. Journal of Applied Ecology, 54 (5), 1459–1468. https://doi.org/10.1111/1365-2664.12857
  399. Camp, R.J., R. Loh, S.P. Berkowitz, K.W. Brinck, J.D. Jacobi, J. Price, S. McDaniel, and L.B. Fortini, 2018: Potential Impacts of Projected Climate Change on Vegetation Management in Hawai`i Volcanoes National Park. U.S. Department of the Interior, National Park Service, 10 pp. https://pubs.er.usgs.gov/publication/70196506
  400. Fortini, L.B. and J.D. Jacobi, 2018: Identifying opportunities for long-lasting habitat conservation and restoration in Hawaii’s shifting climate. Regional Environmental Change, 18 (8), 2391–2402. https://doi.org/10.1007/s10113-018-1342-6
  401. Wada, C.A., L.L. Bremer, K. Burnett, C. Trauernicht, T. Giambelluca, L. Mandle, E. Parsons, C. Weil, N. Kurashima, and T. Ticktin, 2017: Estimating cost-effectiveness of Hawaiian dry forest restoration using spatial changes in water yield and landscape flammability under climate change. Pacific Science, 71 (4), 401–424. https://doi.org/10.2984/71.4.2
  402. von Holle, B., S. Yelenik, and E.S. Gornish, 2020: Restoration at the landscape scale as a means of mitigation and adaptation to climate change. Current Landscape Ecology Reports, 5 (3), 85–97. https://doi.org/10.1007/s40823-020-00056-7
  403. Bremer, L.L., C.A. Wada, S. Medoff, J. Page, K. Falinski, and K.M. Burnett, 2019: Contributions of native forest protection to local water supplies in East Maui. Science of The Total Environment, 688, 1422–1432. https://doi.org/10.1016/j.scitotenv.2019.06.220
  404. Burnett, K.M., T. Ticktin, L.L. Bremer, S.A. Quazi, C. Geslani, C.A. Wada, N. Kurashima, L. Mandle, P.a. Pascua, T. Depraetere, D. Wolkis, M. Edmonds, T. Giambelluca, K. Falinski, and K.B. Winter, 2019: Restoring to the future: Environmental, cultural, and management trade-offs in historical versus hybrid restoration of a highly modified ecosystem. Conservation Letters, 12 (1), e12606. https://doi.org/10.1111/conl.12606
  405. Bremer, L.L., L. Mandle, C. Trauernicht, P.a. Pascua, H.L. McMillen, K. Burnett, C.A. Wada, N. Kurashima, S.A. Quazi, T. Giambelluca, P. Chock, and T. Ticktin, 2018: Bringing multiple values to the table: Assessing future land-use and climate change in North Kona, Hawaiʻi. Ecology and Society, 23 (1), 33. https://doi.org/10.5751/es-09936-230133
  406. CRHI, 2021: Nature-Based Resilience and Adaptation to Climate Change in Hawaiʻi. Climate Ready Hawaiʻi. https://climate.hawaii.gov/wp-content/uploads/2021/04/CRHI-Working-Paper-V5.pdf
  407. Richmond, R.H., Y. Golbuu, and A.J. Shelton III, 2019: Ch. 26. Successful management of coral reef-watershed networks. In: Coasts and Estuaries. Wolanski, E., J.W. Day, M. Elliott, and R. Ramachandran, Eds. Elsevier, 445–459. https://doi.org/10.1016/b978-0-12-814003-1.00026-5
  408. Friedlander, A.M. and C.F. Gaymer, 2021: Progress, opportunities and challenges for marine conservation in the Pacific Islands. Aquatic Conservation: Marine and Freshwater Ecosystems, 31 (2), 221–231. https://doi.org/10.1002/aqc.3464
  409. Loope, L.L., R.F. Hughes, and J.-Y. Meyer, 2013: Ch. 15. Plant invasions in protected areas of tropical Pacific islands, with special reference to Hawaii. In: Plant Invasions in Protected Areas: Patterns, Problems and Challenges. Foxcroft, L.C., P. Pyšek, D.M. Richardson, and P. Genovesi, Eds. Springer, Dordrecht, Netherlands, 313–348. https://doi.org/10.1007/978-94-007-7750-7_15
  410. Gaüzère, P., F. Jiguet, and V. Devictor, 2016: Can protected areas mitigate the impacts of climate change on bird's species and communities? Diversity and Distributions, 22 (6), 625–637. https://doi.org/10.1111/ddi.12426
  411. Lawler, J.J. and J. Hepinstall-Cymerman, 2010: Ch. 15. Conservation planning in a changing climate: Assessing the impacts of potential range shifts on a reserve network. In: Landscape-Scale Conservation Planning. Trombulak, S.C. and R.F. Baldwin, Eds. Springer, Dordrecht, Netherlands, 325–348. https://doi.org/10.1007/978-90-481-9575-6_15
  412. Roberts, C.M., B.C. O’Leary, D.J. McCauley, P.M. Cury, C.M. Duarte, J. Lubchenco, D. Pauly, A. Sáenz-Arroyo, U.R. Sumaila, R.W. Wilson, B. Worm, and J.C. Castilla, 2017: Marine reserves can mitigate and promote adaptation to climate change. Proceedings of the National Academy of Sciences of the United States of America, 114 (24), 6167–6175. https://doi.org/10.1073/pnas.1701262114
  413. Virkkala, R., J. Pöyry, R.K. Heikkinen, A. Lehikoinen, and J. Valkama, 2014: Protected areas alleviate climate change effects on northern bird species of conservation concern. Ecology and Evolution, 4 (15), 2991–3003. https://doi.org/10.1002/ece3.1162
  414. Judge, S.W., C.C. Warren, R.J. Camp, L.K. Berthold, H.L. Mounce, P.J. Hart, and R.J. Monello, 2021: Population estimates and trends of three Maui Island‐endemic Hawaiian honeycreepers. Journal of Field Ornithology, 92 (2), 115–126. https://doi.org/10.1111/jofo.12364
  415. Paxton, E.H., R.J. Camp, P.M. Gorresen, L.H. Crampton, D.L. Leonard, and E.A. VanderWerf, 2016: Collapsing avian community on a Hawaiian island. Science Advances, 2 (9), e1600029. https://doi.org/10.1126/sciadv.1600029
  416. Liao, W., C.T. Atkinson, D.A. LaPointe, and M.D. Samuel, 2017: Mitigating future avian malaria threats to Hawaiian forest birds from climate change. PLoS ONE, 12 (1), e0168880. https://doi.org/10.1371/journal.pone.0168880
  417. Paxton, E.H., M. Laut, S. Enomoto, and M. Bogardus, 2022: Hawaiian Forest Bird Conservation Strategies for Minimizing the Risk of Extinction: Biological and Biocultural Considerations. Hawaii Cooperative Studies Unit Technical Report 103. University of Hawai‘i at Hilo, Hawai‘i Cooperative Studies Unit, 119 pp. https://pubs.er.usgs.gov/publication/70230509
  418. Paxton, E.H., M. Laut, J.P. Vetter, and S.J. Kendall, 2018: Research and management priorities for Hawaiian forest birds. The Condor, 120 (3), 557–565. https://doi.org/10.1650/condor-18-25.1
  419. Samuel, M.D., W. Liao, C.T. Atkinson, and D.A. LaPointe, 2020: Facilitated adaptation for conservation – Can gene editing save Hawaii’s endangered birds from climate driven avian malaria? Biological Conservation, 241, 108390. https://doi.org/10.1016/j.biocon.2019.108390
  420. Fortini, L.B., L.R. Kaiser, and D.A. LaPointe, 2020: Fostering real-time climate adaptation: Analyzing past, current, and forecast temperature to understand the dynamic risk to Hawaiian honeycreepers from avian malaria. Global Ecology and Conservation, 23, 01069. https://doi.org/10.1016/j.gecco.2020.e01069
  421. Fantle-Lepczyk, J., L. Crampton, A. Taylor, D. Duffy, and S. Conant, 2020: An analysis of translocation regimes for the endangered puaiohi Myadestes palmeri. Endangered Species Research, 41, 105–118. https://doi.org/10.3354/esr01011
  422. Fortini, L.B., L.R. Kaiser, A.E. Vorsino, E.H. Paxton, and J.D. Jacobi, 2017: Assessing the potential of translocating vulnerable forest birds by searching for novel and enduring climatic ranges. Ecology and Evolution, 7 (21), 9119–9130. https://doi.org/10.1002/ece3.3451
  423. Rivera, S.N., L.B. Fortini, S. Plentovich, and M.R. Price, 2021: Perceived barriers to the use of assisted colonization for climate sensitive species in the Hawaiian Islands. Environmental Management, 68 (3), 329–339. https://doi.org/10.1007/s00267-021-01491-w
  424. van Dooren, T., 2019: Moving birds in Hawai’i: Assisted colonisation in a colonised land. Cultural Studies Review, 25 (1), 41–64. https://doi.org/10.5130/csr.v25i1.6392
  425. Kueffer, C. and K. Kinney, 2017: What is the importance of islands to environmental conservation? Environmental Conservation, 44 (4), 311–322. https://doi.org/10.1017/s0376892917000479
  426. McMillen, H., T. Ticktin, and H.K. Springer, 2017: The future is behind us: Traditional ecological knowledge and resilience over time on Hawai‘i Island. Regional Environmental Change, 17 (2), 579–592. https://doi.org/10.1007/s10113-016-1032-1
  427. Winter, K.B., K. Beamer, M.B. Vaughan, A.M. Friedlander, M.H. Kido, A.N. Whitehead, M.K.H. Akutagawa, N. Kurashima, M.P. Lucas, and B. Nyberg, 2018: The moku system: Managing biocultural resources for abundance within social-ecological regions in Hawaiʻi. Sustainability, 10 (10), 3554. https://doi.org/10.3390/su10103554
  428. Winter, K.B., T. Ticktin, and S.A. Quazi, 2020: Biocultural restoration in Hawaiʻi also achieves core conservation goals. Ecology and Society, 25 (1). https://doi.org/10.5751/es-11388-250126
  429. Keali‘ikanaka‘oleohaililani, K., N. Kurashima, K.S. Francisco, C.P. Giardina, R.P. Louis, H. McMillen, C.K. Asing, K. Asing, T.A. Block, M. Browning, K. Camara, L. Camara, M.L. Dudley, M. Frazier, N. Gomes, A.E. Gordon, M. Gordon, L. Heu, A. Irvine, N. Kaawa, S. Kirkpatrick, E. Leucht, C.H. Perry, J. Replogle, L.-L. Salbosa, A. Sato, L. Schubert, A. Sterling, A.L. Uowolo, J. Uowolo, B. Walker, A.N. Whitehead, and D. Yogi, 2018: Ritual + sustainability science? A portal into the science of Aloha. Sustainability, 10 (10), 3478. https://doi.org/10.3390/su10103478
  430. Diver, S., M. Vaughan, M. Baker-Médard, and H. Lukacs, 2019: Recognizing “reciprocal relations” to restore community access to land and water. International Journal of the Commons, 13 (1), 400–429. https://doi.org/10.18352/ijc.881
  431. Vaughan, M.B. and P.M. Vitousek, 2013: Mahele: Sustaining communities through small-scale inshore fishery catch and sharing networks. Pacific Science, 67 (3), 329–344. https://doi.org/10.2984/67.3.3
  432. Kamelamela, K.L., H.K. Springer, R. Ku'ulei Keakealani, M.U. Ching, T. Ticktin, R.D. Ohara, E.W. Parsons, E.D. Adkins, K.S. Francisco, and C. Giardina, 2022: Kōkua aku, Kōkua mai: An Indigenous consensus-driven and place-based approach to community led dryland restoration and stewardship. Forest Ecology and Management, 506, 119949. https://doi.org/10.1016/j.foreco.2021.119949
  433. Morishige, K., P. Andrade, P. Pascua, K. Steward, E. Cadiz, L. Kapono, and U. Chong, 2018: Nā Kilo ʻĀina: Visions of biocultural restoration through Indigenous relationships between people and place. Sustainability, 10 (10), 3368. https://doi.org/10.3390/su10103368
  434. Harmon, K.C., K.B. Winter, N. Kurashima, C.H. Fletcher, H.H. Kane, and M.R. Price, 2021: The role of indigenous practices in expanding waterbird habitat in the face of rising seas. Anthropocene, 34, 100293. https://doi.org/10.1016/j.ancene.2021.100293
  435. Andrade, P. and K. Morishige, 2022: Huli‘a: Every place has a story ... Let’s listen. Parks Stewardship Forum, 38 (2). https://doi.org/10.5070/p538257525
  436. Andrade, P., K. Morishige, A. Mau, L. Kapono, and E.C. Franklin, 2022: Re-imagining contemporary conservation to support ‘Āina Momona: Productive and thriving communities of people, place, and natural resources. Parks Stewardship Forum, 38 (2). https://doi.org/10.5070/p538257511
  437. Kane, H.H., C.H. Fletcher, E.E. Cochrane, J.X. Mitrovica, S. Habel, and M. Barbee, 2017: Coastal plain stratigraphy records tectonic, environmental, and human habitability changes related to sea-level drawdown, ‘Upolu, Sāmoa. Quaternary Research, 87 (2), 246–257. https://doi.org/10.1017/qua.2017.2
  438. Kayanne, H., T. Yasukochi, T. Yamaguchi, H. Yamano, and M. Yoneda, 2011: Rapid settlement of Majuro Atoll, central Pacific, following its emergence at 2000 years CalBP. Geophysical Research Letters, 38 (20). https://doi.org/10.1029/2011gl049163
  439. Morgan, W.N., 1988: Prehistoric Architecture in Micronesia. University of Texas Press, New York, USA. https://doi.org/10.7560/765061
  440. Pukui, M.K., 1983: ʻŌlelo Noʻeau: Hawaiian Proverbs and Poetical Sayings. Bishop Museum Press, 372 pp. https://bishopmuseumpress.org/products/olelo-no-eau-hawaiian-proverbs-poetical-sayings-1
  441. Hui Mālama Loko I‘a, 2020: Loko I‘a Needs Assessment. University of Hawai‘i, Sea Grant College Program and Pacific Islands Climate Adaptation Science Center. https://seagrant.soest.hawaii.edu/loko-i%CA%BBa-needs-assessment/
  442. Kurashima, N., L. Fortini, and T. Ticktin, 2019: The potential of Indigenous agricultural food production under climate change in Hawaiʻi. Nature Sustainability, 2 (3), 191–199. https://doi.org/10.1038/s41893-019-0226-1
  443. Pascua, P., H. McMillen, T. Ticktin, M. Vaughan, and K.B. Winter, 2017: Beyond services: A process and framework to incorporate cultural, genealogical, place-based, and Indigenous relationships in ecosystem service assessments. Ecosystem Services, 26, 465–475. https://doi.org/10.1016/j.ecoser.2017.03.012
  444. Office of Hawaiian Affairs, National Oceanic and Atmospheric Administration, U.S. Fish and Wildlife Service, and State of Hawai‘i, 2021: Mai Ka Pō Mai: A Native Hawaiian Guidance Document for Papahānaumokuākea Marine National Monument. Office of Hawaiian Affairs, Honolulu, HI. https://www.papahanaumokuakea.gov/new-heritage/maikapomai/
  445. Trauernicht, C., T. Ticktin, H. Fraiola, Z. Hastings, and A. Tsuneyoshi, 2018: Active restoration enhances recovery of a Hawaiian mesic forest after fire. Forest Ecology and Management, 411, 1–11. https://doi.org/10.1016/j.foreco.2018.01.005
  446. MacLeod, L., 2021: More than personal communication: Templates for citing Indigenous elders and knowledge keepers. KULA: Knowledge Creation, Dissemination, and Preservation Studies, 5 (1). https://doi.org/10.18357/kula.135
  447. Carroll, S.R., E. Herczog, M. Hudson, K. Russell, and S. Stall, 2021: Operationalizing the CARE and FAIR Principles for Indigenous Data Futures. Scientific Data, 8 (1), 108. https://doi.org/10.1038/s41597-021-00892-0
  448. Hudson, M., N.A. Garrison, R. Sterling, N.R. Caron, K. Fox, J. Yracheta, J. Anderson, P. Wilcox, L. Arbour, A. Brown, M. Taualii, T. Kukutai, R. Haring, B. Te Aika, G.S. Baynam, P.K. Dearden, D. Chagné, R.S. Malhi, I. Garba, N. Tiffin, D. Bolnick, M. Stott, A.K. Rolleston, L.L. Ballantyne, R. Lovett, D. David-Chavez, A. Martinez, A. Sporle, M. Walter, J. Reading, and S.R. Carroll, 2020: Rights, interests and expectations: Indigenous perspectives on unrestricted access to genomic data. Nature Reviews Genetics, 21 (6), 377–384. https://doi.org/10.1038/s41576-020-0228-x
  449. Taylor, K.E., R.J. Stouffer, and G.A. Meehl, 2012: An overview of CMIP5 and the experiment design. Bulletin of the American Meteorological Society, 93 (4), 485–498. https://doi.org/10.1175/bams-d-11-00094.1
  450. Eyring, V., S. Bony, G.A. Meehl, C.A. Senior, B. Stevens, R.J. Stouffer, and K.E. Taylor, 2016: Overview of the Coupled Model Intercomparison Project Phase 6 (CMIP6) experimental design and organization. Geoscientific Model Development, 9 (5), 1937–1958. https://doi.org/10.5194/gmd-9-1937-2016
  451. Strauch, A.M., R.A. MacKenzie, C.P. Giardina, and G.L. Bruland, 2015: Climate driven changes to rainfall and streamflow patterns in a model tropical island hydrological system. Journal of Hydrology, 523, 160–169. https://doi.org/10.1016/j.jhydrol.2015.01.045
  452. Bell, J. and T. Bahri, 2018: A new climate change vulnerability assessment for fisheries and aquaculture. SPC Fisheries Newsletter, 156, 43–56. https://www.conservation.org/docs/default-source/publication-pdfs/a-new-climate-change-vulnerability-assessment-for-fisheries-and-aquaculture.pdf?status=master&sfvrsn=d209baa7_2
  453. Savage, A., H. Bambrick, and D. Gallegos, 2020: From garden to store: Local perspectives of changing food and nutrition security in a Pacific Island country. Food Security, 12 (6), 1331–1348. https://doi.org/10.1007/s12571-020-01053-8
  454. Bird, Z., V. Iese, H.J. Des Combes, M. Wairiu, and L.B.K. Yuen, 2022: Assessing the impacts of climate change on domestic crop production: Experience and perception of local farmers in North Malaita, Solomon Islands. Journal of Interdisciplinary Research, 6 (1), 77–98. https://doi.org/10.26021/12507
  455. Xue, L., Y. Wang, A.J. Newman, K. Ikeda, R.M. Rasmussen, T.W. Giambelluca, R.J. Longman, A.J. Monaghan, M.P. Clark, and J.R. Arnold, 2020: How will rainfall change over Hawai‘i in the future? High-resolution regional climate simulation of the Hawaiian Islands. Bulletin of Atmospheric Science and Technology, 1 (3), 459–490. https://doi.org/10.1007/s42865-020-00022-5
  456. Gingerich, S.B., 2013: The Effects of Withdrawals and Drought on Groundwater Availability in the Northern Guam Lens Aquifer, Guam. USGS Scientific Investigations Report 2013-5216. U.S. Geological Survey, 76 pp. https://doi.org/10.3133/sir20135216
  457. Izuka, S.K., K. Rotzoll, and T. Nishikawa, 2021: Volcanic Aquifers of Hawai‘i—Construction and Calibration of Numerical Models for Assessing Groundwater Availability on Kaua‘i, O‘ahu, and Maui. USGS Scientific Investigations Report 2020-5126. U.S. Geological Survey, 63 pp. https://doi.org/10.3133/sir20205126
  458. Bailey, R.T., J.W. Jenson, D. Rubinstein, and A.E. Olsen, 2008: Groundwater Resources of Atoll Islands: Observations, Modeling, and Management. Technical Report No. 119. University of Guam, Water and Environmental Research Institute of the Western Pacific. https://weri-cdn.uog.edu/wp-content/PDFs/TRs/WERI%20TR%20119%20-%20Bailey%20et%20al%202008.pdf
  459. USGCRP, 2016: The Impacts of Climate Change on Human Health in the United States: A Scientific Assessment. Crimmins, A., J. Balbus, J.L. Gamble, C.B. Beard, J.E. Bell, D. Dodgen, R.J. Eisen, N. Fann, M.D. Hawkins, S.C. Herring, L. Jantarasami, D.M. Mills, S. Saha, M.C. Sarofim, J. Trtanj, and L. Ziska, Eds. U.S. Global Change Research Program, Washington, DC, 312 pp. https://doi.org/10.7930/j0r49nqx
  460. Cinner, J.E. and M.L. Barnes, 2019: Social dimensions of resilience in social-ecological systems. One Earth, 1 (1), 51–56. https://doi.org/10.1016/j.oneear.2019.08.003
  461. Cohen, M.C.L., R.J. Lara, E. Cuevas, E.M. Oliveras, and L. Da Silveira Sternberg, 2016: Effects of sea-level rise and climatic changes on mangroves from southwestern littoral of Puerto Rico during the middle and late Holocene. CATENA, 143, 187–200. https://doi.org/10.1016/j.catena.2016.03.041
  462. Nunn, P.D., R. McLean, A. Dean, T. Fong, V. Iese, M. Katonivualiku, C. Klöck, I. Korovulavula, R. Kumar, and T. Tabe, 2020: Ch. 14. Adaptation to climate change: Contemporary challenges and perspectives. In: Climate Change and Impacts in the Pacific. Kumar, L., Ed. Springer, Cham, Switzerland, 499–524. https://doi.org/10.1007/978-3-030-32878-8_14
  463. Warrick, O., W. Aalbersberg, P. Dumaru, R. McNaught, and K. Teperman, 2017: The ‘Pacific Adaptive Capacity Analysis Framework’: Guiding the assessment of adaptive capacity in Pacific Island communities. Regional Environmental Change, 17 (4), 1039–1051. https://doi.org/10.1007/s10113-016-1036-x
  464. Moser, S.C., 2019: The adaptive mind: Psychosocial support for professionals working on the frontlines of climate change. In: AGU Fall Meeting Abstracts. American Geophysical Union. https://ui.adsabs.harvard.edu/abs/2019agufm.u13b..06m/abstract
  465. Sweet, W.V., R.E. Kopp, C.P. Weaver, J. Obeysekera, R.M. Horton, E.R. Thieler, and C. Zervas, 2017: Global and Regional Sea Level Rise Scenarios for the United States. NOAA Technical Report NOS CO-OPS 083. National Oceanic and Atmospheric Administration, National Ocean Service, Silver Spring, MD, 75 pp. https://repository.library.noaa.gov/view/noaa/18399
  466. Bertana, A., 2020: The role of power in community participation: Relocation as climate change adaptation in Fiji. Environment and Planning C: Politics and Space, 38 (5), 902–919. https://doi.org/10.1177/2399654420909394
  467. Donner, S.D. and S. Webber, 2014: Obstacles to climate change adaptation decisions: A case study of sea-level rise and coastal protection measures in Kiribati. Sustainability Science, 9 (3), 331–345. https://doi.org/10.1007/s11625-014-0242-z
  468. Hermann, E. and W. Kempf, 2017: Climate change and the imagining of migration: Emerging discourses on Kiribati’s land purchase in Fiji. The Contemporary Pacific, 29 (2), 231–263. http://hdl.handle.net/10125/58115
  469. McMichael, C., 2020: Human mobility, climate change, and health: Unpacking the connections. The Lancet Planetary Health, 4 (6), e217–e218. https://doi.org/10.1016/s2542-5196(20)30125-x
  470. Piggott-McKellar, A.E., K.E. McNamara, P.D. Nunn, and S.T. Sekinini, 2019: Moving people in a changing climate: Lessons from two case studies in Fiji. Social Sciences, 8 (5), 133. https://doi.org/10.3390/socsci8050133
  471. Tabe, T., 2019: Climate change migration and displacement: Learning from past relocations in the Pacific. Social Sciences, 8 (7), 218. https://doi.org/10.3390/socsci8070218
  472. Rubinstein, D.H. and M.J. Levin, 1992: Micronesian migration to Guam: Social and economic characteristics. Asian and Pacific Migration Journal, 1 (2), 350–385. https://doi.org/10.1177/011719689200100208
  473. Paudel, S., S. Mansfield, L.F. Villamizar, T.A. Jackson, and S.D.G. Marshall, 2021: Can biological control overcome the threat from newly invasive coconut rhinoceros beetle populations (Coleoptera: Scarabaeidae)? A review. Annals of the Entomological Society of America, 114 (2), 247–256. https://doi.org/10.1093/aesa/saaa057
  474. Caasi, J.A.S., A.L. Guerrero, K. Yoon, L.J.C. Aquino, A. Moore, H. Oh, J. Rychtář, and D. Taylor, 2023: A mathematical model of invasion and control of coconut rhinoceros beetle Oryctes rhinoceros (L.) in Guam. Journal of Theoretical Biology, 570, 111525. https://doi.org/10.1016/j.jtbi.2023.111525
  475. Marshall, S.D.G., A. Moore, M. Vaqalo, A. Noble, and T.A. Jackson, 2017: A new haplotype of the coconut rhinoceros beetle, Oryctes rhinoceros, has escaped biological control by Oryctes rhinoceros nudivirus and is invading Pacific Islands. Journal of Invertebrate Pathology, 149, 127–134. https://doi.org/10.1016/j.jip.2017.07.006
  476. Soto, I., R.N. Cuthbert, A. Kouba, C. Capinha, A. Turbelin, E.J. Hudgins, C. Diagne, F. Courchamp, and P.J. Haubrock, 2022: Global economic costs of herpetofauna invasions. Scientific Reports, 12 (1), 10829. https://doi.org/10.1038/s41598-022-15079-9
  477. Fritts, T.H., 2002: Economic costs of electrical system instability and power outages caused by snakes on the Island of Guam. International Biodeterioration & Biodegradation, 49 (2), 93–100. https://doi.org/10.1016/S0964-8305(01)00108-1
  478. Chu, E.K. and C.E.B. Cannon, 2021: Equity, inclusion, and justice as criteria for decision-making on climate adaptation in cities. Current Opinion in Environmental Sustainability, 51, 85–94. https://doi.org/10.1016/j.cosust.2021.02.009
  479. Doswald, N., R. Munroe, D. Roe, A. Giuliani, I. Castelli, J. Stephens, I. Möller, T. Spencer, B. Vira, and H. Reid, 2014: Effectiveness of ecosystem-based approaches for adaptation: Review of the evidence-base. Climate and Development, 6 (2), 185–201. https://doi.org/10.1080/17565529.2013.867247
  480. Sudmeier-Rieux, K., T. Arce-Mojica, H.J. Boehmer, N. Doswald, L. Emerton, D.A. Friess, S. Galvin, M. Hagenlocher, H. James, P. Laban, C. Lacambra, W. Lange, B.G. McAdoo, C. Moos, J. Mysiak, L. Narvaez, U. Nehren, P. Peduzzi, F.G. Renaud, S. Sandholz, L. Schreyers, Z. Sebesvari, T. Tom, A. Triyanti, P. van Eijk, M. van Staveren, M. Vicarelli, and Y. Walz, 2021: Scientific evidence for ecosystem-based disaster risk reduction. Nature Sustainability, 4 (9), 803–810. https://doi.org/10.1038/s41893-021-00732-4
  481. Oppenheimer, M., B.C. Glavovic, J. Hinkel, R. van de Wal, A.K. Magnan, A. Abd-Elgawad, R. Cai, M. Cifuentes-Jara, R.M. DeConto, T. Ghosh, J. Hay, F. Isla, B. Marzeion, B. Meyssignac, and Z. Sebesvari, 2019: Ch. 4. Sea level rise and implications for low-lying islands, coasts and communities. In: IPCC Special Report on the Ocean and Cryosphere in a Changing Climate. Pörtner, H.-O., D.C. Roberts, V. Masson-Delmotte, P. Zhai, M. Tignor, E. Poloczanska, K. Mintenbeck, A. Alegría, M. Nicolai, A. Okem, J. Petzold, B. Rama, and N.M. Weyer, Eds. Cambridge University Press, Cambridge, UK and New York, NY, USA, 321–445. https://doi.org/10.1017/9781009157964.006
  482. Renaud, F.G., K. Sudmeier-Rieux, M. Estrella, and U. Nehren, Eds., 2016: Ecosystem-Based Disaster Risk Reduction and Adaptation in Practice. Springer, Cham, Switzerland, 598 pp. https://doi.org/10.1007/978-3-319-43633-3
  483. Sasmito, S.D., D. Murdiyarso, D.A. Friess, and S. Kurnianto, 2016: Can mangroves keep pace with contemporary sea level rise? A global data review. Wetlands Ecology and Management, 24 (2), 263–278. https://doi.org/10.1007/s11273-015-9466-7
  484. Zeng, Y., D.A. Friess, T.V. Sarira, K. Siman, and L.P. Koh, 2021: Global potential and limits of mangrove blue carbon for climate change mitigation. Current Biology, 31 (8), 1737–1743. https://doi.org/10.1016/j.cub.2021.01.070
  485. Atkinson, C.T., R.B. Utzurrum, D.A. Lapointe, R.J. Camp, L.H. Crampton, J.T. Foster, and T.W. Giambelluca, 2014: Changing climate and the altitudinal range of avian malaria in the Hawaiian Islands – An ongoing conservation crisis on the island of Kaua'i. Global Change Biology, 20 (8), 2426–2436. https://doi.org/10.1111/gcb.12535
  486. Samuel, M.D., P.H.F. Hobbelen, F. DeCastro, J.A. Ahumada, D.A. LaPointe, C.T. Atkinson, B.L. Woodworth, P.J. Hart, and D.C. Duffy, 2011: The dynamics, transmission, and population impacts of avian malaria in native Hawaiian birds: A modeling approach. Ecological Applications, 21 (8), 2960–2973. https://doi.org/10.1890/10-1311.1

Previous Chapter
View All Figures
Next Chapter

Likelihood

Virtually Certain Very Likely Likely As Likely as Not Unlikely Very Unikely Exceptionally Unlikely
99%–100% 90%–100% 66%–100% 33%–66% 0%–33% 0%–10% 0%–1%

Confidence Level

Very High High Medium Low
  • Strong evidence (established theory, multiple sources, well-documented and accepted methods, etc.)
  • High consensus
  • Moderate evidence (several sources, some consistency, methods vary and/or documentation limited, etc.)
  • Medium consensus
  • Suggestive evidence (a few sources, limited consistency, methods emerging, etc.)
  • Competing schools of thought
  • Inconclusive evidence (limited sources, extrapolations, inconsistent findings, poor documentation and/or methods not tested, etc.)
  • Disagreement or lack of opinions among experts

GlobalChange.gov is made possible by our participating agencies

Department of Agriculture Department of Commerce Department of Defense Department of Energy Department of Health and Human Services Department of Homeland Security Department of Interior Department of State Department of Transportation Environmental Protection Agency NASA National Science Foundation Smithsonian Institute Agency for International Development
  • About USGCRP
  • FOIA requests
  • No FEAR Act
  • Accessibility
  • Privacy Policy
  • Copyright
  • Contact Us
  • Site Map
Looking for U.S. government information and services?
Visit USA.gov