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Hawaiian High Islands Ecoregion
This page last revised 04 September 2006 -- S.M.Gon III

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feral pig
Feral ungulates such as pigs (Sus scrofa) represent a disturbance not present in pre-human Hawai‘i.

Miconia calvescens -- invasive alien weedHabitat-modifying weeds such as the alien melastome Miconia calvescens represent a major threat to native biodiversity.

Remote area management
Bringing active threat abatement management to priority conservation areas is the primary goal.

Threats

Assessing threats

The greatest, most pervasive threats to the Hawaiian High Islands ecoregion portfolio are feral ungulates and invasive, habitat-modifying weeds.  Threats such as fire, residential development, and military training are important and highly ranked at specific locations.

The 1998 ecoregion plan identified and described the general suite of threats in the ecoregion. ERA II builds on that foundation and ranks the highest priority threats for each conservation area. Threats include some that are pervasive across all conservation areas in the archipelago and some that are specific to particular places (see table below). 

Threat summary

The key stress in vegetated ecological systems in Hawai‘i is change in comp­o­si­tion and structure, typically through sim­pli­fi­cation and loss of native diversity, followed by loss of understory (and eventually canopy) structure. The main sources of stress include both biological and anthropogenic factors, discussed below.

Invasive alien species:
The continuing invasion of alien (non-native) weeds, predators, herbi­vores, patho­gens, and com­pet­i­tors into native eco­systems is the engine that currently drives the Hawaiian extinction crisis.

Since the establishment of forest reserves encompassing nearly all re­maining native forests during the first three decades of the 20th century, alien invasion — not direct habitat de­struc­tion by humans—has been the domi­nant threat to native species and eco­systems in the Hawaiian Islands.

Hawai‘i is extra­ordi­na­ri­ly vul­nerable to human-ac­cel­er­ated alien species in­vasions due to:

1)       the break-down of its geographic isolation as it became the hub of Pacific travel and trade;

2)       an exceptional range of hospitable habitats for invaders to occupy.

The estimated rate for suc­cess­ful, new colonization of the islands by a plant or animal species before human arrival was once every 25,000 - 50,000 years.  In contrast, over the past 30 years, newly established species have been re­cord­ed in Hawai‘i at the rate of once every 18 days. The existing com­ple­ment of es­tab­lished invasive aliens has the ca­pa­city to overwhelm most remaining native habitat if left unchecked.

(continued next column)


pig damage in forest understory
Understory obliteration by feral pigs in a montane wet forest community.

Over human history in the islands, several major groups of alien species have emerged as the most damaging to native ecosystems and species:

o        Ungulates – lacking any large native herbivorous mammals, the Hawaiian flora is not adapted to ungulate brows­ing or trampling. Feral pigs, goats, sheep, deer, and cattle were responsible for de­struc­tion of lowland ecosystems, and continue to degrade re­main­ing native ecological systems.

o        Invasive weeds – through a his­tory of increasing introduction of alien plants, there are now more species of nat­u­ral­ized alien vas­cular plants in the wilds of Hawai‘i than there are native species. Perhaps 200 of these are ex­treme­ly aggressive, habitat-modifying weeds.

o        Predators – small mammals such as rats, mongoose, and feral cats prey on native birds. Rats are im­pli­cated as wholesale vegetation modifiers via selective seed pre­da­tion. Predatory invertebrates such as ants and other social hymenoptera have greatly disrupted in­ver­te­brate communities at all elevations, par­tic­ularly in the lowlands.

For these reasons, conservation in Hawai‘i de­pends more than anything on keep­ing re­maining, rela­tively uninvaded native areas intact, stem­ming the es­tab­lish­ment of new in­va­sive species, and devising practical strategies to limit the impact of widely-established species.



lehua blossom
A summary of threats across conservation areas in the Hawaiian ecoregion reveals that alien species such as ungulates and weeds are prominent and ubiquitous, with other threats active in specific locations.Threat assessment followed Conservation Area Planning (CAP) guidelines.

THREAT ASSESSMENT SUMMARY: Hawaiian Conservation Areas

Threat
KAU

WAI

KOO

EMO

WMA

EMA

KOH

MK

WML

K-K

KON

P-P
 Ungulates
H

H

H

H

H

H

H

H

H

H

H

H
Weeds
H

VH

VH

H

H

H

H

H

VH

H

H

H
Fire
L

H

M

H

M

L

L

M

L

L

H

VH
Small Mammals
M

H

M

L

L

M

L

M

M

M

M

L
Pathogens
M

L

L

L

L

M

L

M

M

M

M

L
Development
L

M

M

L

L

L

L

L

H

L

H

L
Military Training
L

H

M

L

L

L

L

L

L

L

L

H
Recreational Use
L

L

L

L

L

L

L

L

L

L

L

L
Stream Diversion
L

NA

L

L

M

M

L

M

NA

NA

NA

NA
Overharvesting
L

L

L

L

L

L

L

L

L

L

L

L
Logging
L

L

L

L

L

L

L

M

L

L

H

L
Grazing
L

L

L

L

L

L

M

M

L

L

H

M
Overall rank:
M

H

H

M

M

M

M

H

H

M

H

H
Abbreviations: Islands and Conservation Areas: KAU = Kaua‘i; WAI = Wai‘anae; KOO = Ko‘olau ; EMO = East Moloka‘i;  WMA = West Maui; EMA = East Maui; KOH = Kohala; MK = Mauna Kea; WML = Windward Mauna Loa; K-K = Ka‘ū-Kapāpala; KON = Kona; P-P = Pōhakuloa - Pu‘u Wa‘awa‘a.
Threat Ranks:
VH = Very High, H = High, M = Medium, L = Low.


Wildfire is not a natural process in Hawai'i Wildfire in Hawai'i is invariably followed by invasion by fire-adapted alien grasses and shrubs, creating a cycle of destruction for native species and ecosystems. 

mosquito
Mosquitos carry diseases such as avian malaria; deadly to endangered forest birds.

feral ungulates
Goats and sheep are a prevailing threat to drier native areas in Hawai‘i.

urban sprawl in Honolulu, O'ahu
Development remains a threat on O'ahu, where 80% of the state's population resides.

Threat Summary (continued from above)

Fire:  Wildfire is an uncommon natural occurrence in Hawai‘i, where ground-strike lightning is rare and wet plant communities cover large areas.  Fire-adapted aliens (especially grasses and short-lived shrubs) are established in lower, leeward slopes and some subalpine areas.  Normally ignited by people, these weeds fuel major wildfires that can carry into native forests. Native forests are destroyed and replaced with fire-adapted weeds in a trend that increases the range and intensity of these fires. 

Rats are bird predators
Rodents are important egg predators in forest bird concentration areas.

Small Mammals: There are no native small mammals (e.g., rodents, cats, dogs, rabbits, mongooses) in Hawai‘i, and the ecological effects of either herbivorous, omnivorous, or predatory small mammals is to reduce populations of native species, sometimes to extinction. Rodents are implicated in damage to lowland forests via seed predation, as well as on both ground-nesting seabirds and forest birds. Feral cats and dogs impose similar impacts. Rodents seem particularly damaging in the Wai'anae conservation area of O‘ahu, where they affect endangered tree snails, rare native plants, and an endangered forest bird, the ‘elepaio (Chasiempis  sandwichensis gayi).

Pathogens (including invertebrate pests): Diseases and pests can play an important role in reduction of viability of native species, and indirectly, the natural communities and ecological systems comprised of these species. Pathogens and pests related to declines in native species include mosquitoes and mosquito-borne diseases (avian malaria and pox), ants (various species), Erythrina gall wasp (Quadrastichus erythrinae), two-spotted leafhopper (Sophonia rufofascia), slugs (various species), and black twig borer (Xylosandrus compactus). Often the role of pathogens is tied to other threats. For example, avian diseases affecting native forest bird concentrations are spread by mosquitos, and spread of mosquitos into forest bird habitat is tied to wallows of feral pigs that create mosquito breeding sites where none otherwise exist.

Development : Widespread conversion and development of the lowlands of the Hawaiian ecoregion took place from prehistoric times to the first half of the twentieth century. Following statehood, strong conservation zoning has largely limited development of natural areas and forest reserves, but incremental conversion of lowland native areas continues on the most densely populated island (O‘ahu), as well as the largest island (Hawai‘i), particularly in the Windward Mauna Loa and Kona conservation areas.

(continued next column)

Military training activities:  Live-fire training, large-scale troop movements, and heavy equipment operation are serious threats to native species at U.S. Army training facilities in the Oahu and Hawai‘i conservation areas.  Training operations have resulted in clearing of native vegetation, increased wildfire, and the introduction and spread of unwanted alien species.  The Army has instituted an ecosystem management program to mitigate these impacts, and is now among the state’s most active and well-funded stewards of native systems.

Recreational use: Typical recreational uses of native ecosystems include hiking, camping, and off-road vehicle touring. Restrictions on damaging activities in the state conservation district somewhat limits the impacts of recreational use, although indirect effects of recreational activities such as hiking, e.g., spread of invasive weeds, has been documented.

Stream diversion
:  Native stream communities are highly dependent on continuous stream flows to the sea to support the diadromous life cycles of their dominant aquatic animals.  Most of the state’s streams are already partially or fully altered (channelized, diverted, or de-watered via groundwater pumping), and those that remain are vulnerable as the demand for fresh water outstrips the current yield of harvesting. The new Hawai‘i State Water Code provides mechanisms for protecting stream flow, but these mechanisms await their first test cases.

Overharvesting: Most minor forest and stream “commodities” (plant materials for lei making, flower arrangements, and herbal use; stream fishes and invertebrates for food) can be harvested for home and cultural use on a sustainable basis.  These activities are not sustainable at a large, commercial scale in most situations, and are already restricted by permit systems.

Logging:  Although logging and other high-intensity harvesting is no longer widespread in Hawai‘i (most loggable areas were cleared in the last century), these and other clearing practices are important concerns in some conservation areas on Hawai‘i Island. Commercial logging of native koa (Acacia koa), ‘ōhi‘a (Metrosideros spp.), sandalwood (Santalum spp.), and hāpu‘u tree ferns (Cibotium spp.) are approaching the limits of available resources, and the forest products industry supports planting programs to restore former forest lands. 

Grazing:  Clearing of forest for production of cattle has a 200 year history in Hawai‘i. Cattle, being large ungulates, have the same damaging effects on native vegetation as other ungulates, and the devastating effects of cattle in Hawai'i have been well documented. Today, there remain large private ranches, several of which occur within native ecological systems. Ranching-related loss of native ecosystems is active in the Kona conservation area in particular. 

lehua

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