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Tags / Keywords hawaii
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Tags / Keywords yellow-legged hornet
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Invasion - Little Fire Ants in Hawaii (video)

Island and Ocean Ecosystems, BRB

Available Online

Maui Invasive Species Committee (MISC)

Observations of a rapid decline in invasive macroalgal cover linked to green turtle grazing in Hawaiian marine reserve

Available Online

Bahr, Keisha D.

Balazs, George H.

Coffey, Daniel M.

Rodgers, Ku'ulei

Since the 1950's, 19 algal species were intentionally (e.g., aquaculture food) and/or accidentally (e.g., ballast water) introduced into Hawaii (Glenn and Doty 1990).

Eradication programmes complicated by long-lived seed banks: lessons learnt from 15 years of miconia control on O'ahu Island, Hawai'i

Island and Ocean Ecosystems, BRB

Available Online

The invasive tree Miconia calvescens (Melastomataceae) is a priority for control on the Hawaiian Island of O?ahu due to its potential to replace native ??hi?a (Metrosideros polymorpha, Myrtaceae) forests and degrade watershed function if allowed to establish. The O?ahu Invasive Species Committee (OISC) is attempting to eradicate this species from the island of O?ahu. OISC uses a bu?er strategy based on estimated seed dispersal distance to determine the area under surveillance. This strategy has worked well enough to suppress the number of trees reaching reproductive age. The number of mature trees removed annually is now less than the number initially removed when the programme started in 2001. In 2016, just 12 mature trees were removed from 54.71 km2 surveyed compared to 2002, when 40 mature trees were removed from 8.26 km2 surveyed, a 96% drop in mature trees per square kilometre surveyed. However, miconia has a long-lived seed bank and can germinate after 20 years of dormancy in the soil. Funding shortages and gaps in surveys due to refusal of private property owners to allow access have resulted in some long-range extensions. OISCs results suggest that seed bank longevity is an important factor when prioritising invasive species risk and that allocating more resources at the beginning of a programme to eradicate a species with long-lived seed banks may be a better strategy than starting small and expanding.

Analysis of the secondary nest of the yellow-legged hornet found in the Balearic Islands reveals its high adaptability to Mediterranean isolated ecosystems

Island and Ocean Ecosystems, BRB

Available Online

Colomar, V.

Herrera, C.

Leza, M.M.

Marqués, A.

The yellow-legged hornet (Vespa velutina) was detected for the ?rst time in the north of Spain in 2010, but was not detected in Majorca, Balearic Islands until 2015 and only one secondary nest, with 10 combs, was found in the northwest of the island. During 2016, nine more nests were found in the same region. To better understand the biology of V. velutina in isolated conditions, the following objectives were proposed: (I) describe the architecture and structure of nests; (II) analyse the shape of combs and develop a new method to con?rm the circular pattern of breeding; (III) determine the colony size and (IV) determine the succession of workers and sexual individuals throughout the season. For these reasons, nests that were removed were frozen for at least 48 days until analysis. Our results show that this species has a high reproductive potential under isolated conditions. Results reveal that parameters such as weight, height, diameter, number of cells and total individual production are directly related. Moreover, each mature nest can produce up to 9,000 individuals and several hundred potential founder queens. All results inform formulation of an e?cient control or eradication programme in the Balearic Islands, as we are in the early stages of invasion and intervention is essential to eradicate V. velutina on Majorca Island.

Potential economic damage from introduction of Brown Tree Snakes, Boiga Irregularis (Reptilia: Colubridae), to the Islands of Hawaii

Gebhardt, Karen

Kirkpatrick, Katy N.

Shwiff, Stephanie A.

Shwiff, Steven S.

The Brown Tree Snake (Boiga irregularis) has caused ecological and economic damage to Guam, and the snake has the potential to colonize other islands in the Paci c Ocean. This study quanti es the potential economic damage if the snake were translocated, established in the state of Hawaii, and causing damage at levels similar to those on Guam. Damages modeled included costs of medical treatments due to snakebites, snake-caused power outages, and decreased tourism resulting from effects of the snake. Damage caused by presence of the Brown Tree Snake on Guam was used as a guide to estimate potential economic damage to Hawaii from both medical- and power outagerelated damage. To predict tourism impact, a survey was administered to Hawaiian tourists that identi ed tourist responses to potential effects of the Brown Tree Snake. These results were then used in an input-output model to predict damage to the state economy. Summing these damages resulted in an estimated total potential annual damage to Hawaii of between $593 million and $2.14 billion. This economic analysis provides a range of potential damages that policy makers can use in evaluation of future prevention and control programs.

Taking the sting out of the Little Fire Ant in Hawaii

Lee, Donna J.

Leung, PingSun

Motoki, Michael

Nakamoto, Stuart T.

Vanderwoude, Casper

Inthe1990's,LittleFireAnts(LFAs)founditswaytotheislandofHawaii,mostlikelytravelingwithashipmentof potted plantsfrom Florida.These plants weresubsequentlysold toconsumers along theeastcoast of theIsland, alongwithLittleFireAntcolonieslivinginthepottingmedium.LFAisnowthrivingandcontinuestospread.Fifteenyearsaftertheinitialdetectionin1999,LFAhasspreadtoover4000locationsontheislandofHawaiiandhas beenfoundinisolatedlocationsonKauai,Maui,andOahuIslands.Currenteffortsareexpectedtocontaintheinfestations on the otherislands but signi cant additional investment isneeded tohalt therapid spread of LFA on the island of Hawaii. Increased management expenditures can suppress infestations; reduce spread between sectors; and decrease long-term management costs, damages, and stings.| Animmediateexpenditureof$8millioninthenext23yearsplusfollow-upprevention,monitoring,andmitigation treatments will yield $1.210 billion in reduced control costs, $129 million in lowered economic damages, 315 million fewer human sting incidents, and 102 million less pet sting incidents over 10 years.| Over35years,thebene tsinclude$5.496billioninreducedcontrolcosts,$538millionlesseconomicdamages, 2.161 billion fewer human sting incidents, and 762 million fewer pet sting incidents.

Prevention, Eradication and Containment of Invasive Species: Illustrations from Hawaii

Burnett, Kimberly

Kaiser, Brooks

Pitafi, Basharat A.

Roumasset, James

Invasive species change ecosystems and the economic services such ecosystems provide. Optimal policy will minimize the expected damages and costs of prevention and control. We seek to explain policy outcomes as a function of biological and economic factors, using the case of Hawaii to illustrate. First, we consider an existing invasion, Miconia calvescens, a plant with the potential to reduce biodiversity, soil cover, and water availability. We then examine an imminent threat, the potential arrival of the Brown Treesnake (Boiga irregularis). The arrival of the snake to Guam has led to native bird extirpations, power outages, and health costs.

Invasion - Little Fire Ants in Hawaii (video)

Available Online

Maui Invasive Species Committee (MISC)

Hawai'i's invasive species : a guide to invasive plants and animals in the Hawaiian islands

Island and Ocean Ecosystems, BRB

Cowie, Robert H

Staples, George W

Getting involved in caring for Hawaii's Coastal Resources: A community guidebook

Island and Ocean Ecosystems

Available Online

Komoto Jill

Mauka (toward the mountains) and makai (toward the ocean) are not just directional references; they embody our fundamental natural and cultural resources, land and ocean. Hawaiians believe there is a balance between ocean and land. In traditional times, the ocean and its marine life were as well known as the life attributes of the upland areas. This intimate relationship with nature resonates today in the modern principle of sustainability. We continue a strong interconnected, interrelated and interdependent relationship with our natural and cultural resources. Some call it ecosystem-based stewardship.

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