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Tree-of-heaven Ailanthus altissima (Simaroubaceae) Introduction ...

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Eucryptorrhynchus brandti<br />

(Coleoptera: Curculionidae), a<br />

potential biological control agent<br />

<strong>of</strong> tree‐<strong>of</strong>‐<strong>heaven</strong><br />

Tom McAvoy tmcavoy@vt.edu*,<br />

Amy Snyder*, Nathan Herrick, and Scott Salom*<br />

*Department <strong>of</strong> Entomology<br />

College <strong>of</strong> Agriculture and Life Sciences<br />

Virginia Tech<br />

Blacksburg, VA<br />

Biological Control <strong>of</strong> Northeastern Weeds – 2013 Cooperators<br />

Meeting,<br />

Feb. 19, 2013, Trenton, NJ<br />

Known distribution <strong>of</strong> tree‐<strong>of</strong>‐<strong>heaven</strong> in the US.<br />

<strong>Tree</strong>‐<strong>of</strong>‐<strong>heaven</strong> <strong>Ailanthus</strong> <strong>altissima</strong><br />

(<strong>Simaroubaceae</strong>)<br />

Native distribution<br />

Non‐native distribution<br />

Worldwide distribution <strong>of</strong> A. <strong>altissima</strong> (Kowarik and Sӓumel 2007).<br />

<strong>Introduction</strong> into United States<br />

Two introductions from England as an<br />

ornamental:<br />

o 1784 Philadelphia, PA<br />

o 1820 New York City<br />

California Gold Rush mid‐1800’s direct<br />

from China, used as medicinal<br />

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1


Beneficial Uses<br />

City landscapes, tolerant to air pollution and poor soils<br />

Planted in arid climates, strip mines<br />

Developing countries:<br />

o Firewood<br />

o Pulpwood<br />

o Reforestation<br />

Quassinoids, highly oxygenated triterpenes:<br />

o Medicinal anti‐HIV, antitumor, antimalarial properties<br />

o Insecticidal properties, anti‐feedant, growth<br />

regulation<br />

42 nd most abundant species <strong>of</strong> 128 species<br />

0.2 % <strong>of</strong> live volume in Virginia<br />

Negative Impacts<br />

Invasive in forests and along roadways<br />

Very competitive in newly disturbed areas due to :<br />

o Allelopathic properties<br />

o High seed production and suckering<br />

Displaces native plant species<br />

Roots can damage buildings, sidewalks<br />

Costly to control<br />

5,175 km (3,105 mi) surveyed in Virginia<br />

58% <strong>of</strong> every mile surveyed had at least 1 tree‐<strong>of</strong>‐<strong>heaven</strong> stem<br />

39 tree‐<strong>of</strong>‐<strong>heaven</strong> stems / km (62 stems / mi) (McAvoy et al. 2012)<br />

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Management <strong>of</strong> tree‐<strong>of</strong>‐<strong>heaven</strong><br />

Physical – pulling, girdling, digging,<br />

cutting<br />

Chemical ‐ herbicides: glyphosate<br />

(Roundup), triclopyer ester (Garlon)<br />

Biological ‐ fungi and insects<br />

Locations <strong>of</strong> naturally infected and artificially inoculated tree‐<strong>of</strong>‐<br />

<strong>heaven</strong> stands by V. nonalfalfae (Kasson 2012).<br />

Verticillium nonalfalfae Inderb. et al. (formerly V. albo‐<br />

atrum Reinke and Berthold)<br />

Native, soil‐borne, vascular wilt fungus<br />

Resting mycelium can remain dormant<br />

in soil for up to 4 yrs<br />

Long‐range dissemination is limited:<br />

o Wind‐blown leaflets, seeds and insects<br />

Prefers cooler temperatures<br />

Verticillium subspecies or host‐adapted<br />

isolates may attack only certain hosts<br />

Pegg GF, Brady BL. 2002. Verticillium Wilts. Wallingford, UK: CAB International.<br />

Fusarium oxysporum has also been<br />

found to weaken and kill tree‐<strong>of</strong>‐<br />

<strong>heaven</strong><br />

Verticillium nonalfalfae Inderb. et al. (formerly V. albo‐atrum Reinke and Berthold)<br />

Six V. nonalfalfae sites found in Virginia<br />

V. nonalfalfae<br />

Verticillium nonalfalfae<br />

Uninfected<br />

Infected<br />

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3


<strong>Tree</strong>‐<strong>of</strong>‐<strong>heaven</strong> in China is<br />

attacked by:<br />

46 phytophagous arthropods<br />

16 fungi<br />

1 potyvirus<br />

Zheng, H., Wu, Y., Ding, J., Binion, D., Fu, W. and<br />

Reardon, R. (2004), ‘Invasive Plants <strong>of</strong> Asian<br />

Origin Established in the United States and their<br />

Natural Enemies’, Vol 2. Forest Health<br />

Technology Enterprise Team. USDA<br />

Eucryptorrhynchus brandti (Curculionidae)<br />

E. brandti adult feeding<br />

E. brandti egg E. brandti larvae<br />

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E. brandti is a pest <strong>of</strong><br />

tree‐<strong>of</strong>‐<strong>heaven</strong> in<br />

China and is actively<br />

controlled<br />

E. brandti larvae E. brandti emergence holes and adult<br />

Eucryptorrhynchus spp. damaged trees in China<br />

Sapindales<br />

Picramniaceae<br />

Rutaceae<br />

Meliaceae<br />

<strong>Simaroubaceae</strong><br />

Leitneriaceae<br />

Sapindaceae<br />

Anacardiaceae<br />

Buseraceae<br />

Cladogram showing hypothesized relationships in the Order<br />

Sapindales (Judd et al. 2002).<br />

<strong>Tree</strong>‐<strong>of</strong>‐<strong>heaven</strong> plantation in Wuhan, Hubei Eucryptorrhynchus spp. emergence<br />

holes in Wuhan, Hubei<br />

Centrifugal Phylogenetic Strategy (Wapshere 1977)<br />

Sapindales<br />

Leitneriaceae,<br />

Picramniaceae,<br />

Meliaceae,<br />

Rutaceae<br />

<strong>Simaroubaceae</strong>:<br />

Castella,<br />

Holacantha,<br />

Simarouba,<br />

<strong>Tree</strong>‐<strong>of</strong>‐<strong>heaven</strong><br />

2/20/2013<br />

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Native North American, Mexican, and Caribbean<br />

species currently and formerly in <strong>Simaroubaceae</strong><br />

Family<br />

Genus<br />

<strong>Simaroubaceae</strong><br />

Species Common name Distribution<br />

Castela emoryi crucifixion thorn CA, AZ, & Mex.<br />

erecta goatbush TX<br />

polyandra Mex.<br />

Holacantha stewartii Stewart's crucifixion thorn TX<br />

Picrasma antillana bitter ash Carib.<br />

excelsa bitterwood Carib. & Mesoamer.<br />

Quassia amara Amargo, bitter ash, bitterwood Carib.<br />

Simarouba glauca paradise tree FL<br />

Leitneriaceae<br />

tulae aceitillo tree Carib.<br />

Leitneria<br />

Picramniaceae<br />

floridana corkwood AR, FL, GA, MO, TX.<br />

Alvaradoa amorphoides Mexican alvaradoa FL & Mex.<br />

Picramnia pentandra Florida bitterbush FL & Carib<br />

10 Economically important species and 5 Ecologically associated species.<br />

Family<br />

Economically important<br />

Test species Common name<br />

Aceraceae Acer rubrum red maple<br />

Anacardiaceae Mangifera indica Mango<br />

Fabaceae Glycine max Soybean<br />

Fagaceae Quercus alba white oak<br />

Quercus rubra red oak<br />

Juglandaceae Carya glabra pignut hickory<br />

Juglans nigra Black walnut<br />

Magnoliaceae Liriodendron tulipifera tulip poplar<br />

Pinaceae Pinus taeda loblolly pine<br />

Poaceae<br />

Ecologically associated<br />

Zea mays corn<br />

Anacardiaceae Rhus typhina staghorn sumac<br />

Cupressaceae Juniperus virginiana eastern redcedar<br />

Fabaceae Robinia pseudoacacia black locust<br />

Rosaceae Crataegus spp. hawthorne<br />

Prunus serotina black cherry<br />

Adult foliage feeding<br />

Choice Test<br />

1 male and 1 female in each cage, 25oC Allowed to run for 3 days<br />

Newly emerged insects starved for 24 hours<br />

<strong>Tree</strong>‐<strong>of</strong>‐<strong>heaven</strong> and Alvaradoa amorphoides<br />

16 Taxonomically related species tested<br />

Family Test species Common name<br />

<strong>Simaroubaceae</strong> Castela emoryi crucifixion thorn<br />

Simarouba glauca paradise tree<br />

Leitneriaceae Leitneria floridana corkwood<br />

Picramniaceae Alvaradoa amorphoides Mexican alvaradoa<br />

Picramnia pentandra Florida bitterbush<br />

Meliaceae Swietenia mahogoni mahogany<br />

Rutaceae Citrus aurantifolia lime<br />

Citrus aurantium sour orange<br />

Citrus limon lemon<br />

Citrus paradisi grapefruit<br />

Citrus reticulate tangerine<br />

Citrus sinensis sweet orange<br />

Ptelea trifoliata common hoptree<br />

Zanthoxylum americanum northern prickly‐ash<br />

Casimiroa edulis white sapote<br />

Burseraceae Bursera simaruba gumbo limbo<br />

Tests conducted to determine host specificity<br />

• No choice adult foliage feeding<br />

• Choice adult foliage feeding (tree‐<strong>of</strong>‐<br />

<strong>heaven</strong> + nontarget sp.)<br />

negative<br />

Not a host<br />

species<br />

positive<br />

• No choice oviposition<br />

• Larval development<br />

negative<br />

positive<br />

Not a host species Host species<br />

Adult foliage feedingt<br />

No Choice Test<br />

1 male and 1 female in each cage, 25oC Allowed to run for 3 days<br />

Newly emerged insects starved for 24 hours<br />

Alvaradoa amorphoides<br />

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Data Collection: Adult Feeding<br />

<strong>Simaroubaceae</strong><br />

Leitneriaceae<br />

Meliaceae<br />

Rutaceae<br />

Measure foliage feeding<br />

with transparent grid<br />

Burseraceae<br />

Aceraceae<br />

Fagaceae<br />

Juglandaceae<br />

Magnoliaceae<br />

Pinaceae<br />

Anacardiaceae<br />

Two choice (one non‐target + tree‐<strong>of</strong>‐<strong>heaven</strong>) adult feeding test (Herrick et al. 2012)<br />

Larval Development Tests<br />

Cupressaceae<br />

Fabaceae<br />

Rosaceae<br />

Poaceae<br />

<strong>Simaroubaceae</strong><br />

Leitneriaceae<br />

Picramniaceae<br />

Meliaceae<br />

Rutaceae<br />

Burseraceae<br />

Aceraceae<br />

Fagaceae<br />

Juglandaceae<br />

Magnoliaceae<br />

Pinaceae<br />

Anacardiaceae<br />

Cupressaceae<br />

Fabaceae<br />

Rosaceae<br />

Poaceae<br />

No choice adult foliage feeding tests vs. tree‐<strong>of</strong>‐<strong>heaven</strong> (65 mm 2 / day) (Herrick et al. 2012)<br />

Development <strong>of</strong> E. brandti larvae (3, 1 st instars per tree) inoculated<br />

into test species<br />

Family<br />

Species No. <strong>of</strong> trees inoculated<br />

<strong>Simaroubaceae</strong><br />

# trees with larval<br />

development after 4 months<br />

<strong>Ailanthus</strong> <strong>altissima</strong> 10 7<br />

Simarouba glauca<br />

Leitneriaceae<br />

10 0<br />

Leitneria floridana<br />

Rutaceae<br />

10 2<br />

Citrus aurantifolia 10 0<br />

C. aurantium 10 0<br />

C. limon 10 0<br />

C. paradisi 10 0<br />

C. reticulata 10 0<br />

C. sinensis 10 0<br />

E. Brandti shows some acceptance <strong>of</strong> Leitneria floridana, corkwood<br />

Globally ranked G3 (vulnerable;<br />

either very rare and local<br />

throughout its range or found<br />

locally in a restricted range)<br />

In Arkansas and Florida<br />

ranked, S3 (very rare and local or<br />

found locally in a restricted range)<br />

In Missouri ranked, S2<br />

(imperiled because <strong>of</strong> rarity)<br />

In Georgia and Texas, S1<br />

(critically imperiled because <strong>of</strong><br />

extreme rarity)<br />

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Leitneria floridana, corkwood in Florida Oviposition/Survival tests<br />

Oviposition Tests<br />

52 ovipositing females<br />

were caged on corkwood<br />

for 7 days<br />

Results: 47 females were<br />

alive at end <strong>of</strong> test ‐ no<br />

oviposition occurred<br />

Petition for release <strong>of</strong> E. brandti<br />

May 2011 ‐ Submitted petition to APHIS TAG (Technical<br />

Advisory Group)<br />

October 2012 ‐ received response from TAG reviewers:<br />

o 6 approved release<br />

o 6 requested additional information<br />

o 3 recommended no release<br />

o Chairman denied release due to possible impact on<br />

corkwood<br />

Currently we are doing more work on additional test<br />

species and corkwood and will resubmit petition<br />

20 males and 20 females<br />

Newly emerged<br />

Experiments ran until death <strong>of</strong> adults<br />

Results: adults lived a mean <strong>of</strong> 19 days no oviposition<br />

E. brandti has potential for aiding in the spread <strong>of</strong><br />

V. nonalfalfae from tree to tree (Snyder et al. 2012)<br />

Present in feces<br />

Carried externally by adults overwintering<br />

in infected soil<br />

Adults can infect tree‐<strong>of</strong>‐<strong>heaven</strong> seedlings<br />

after ingestion and by tarsal contact with<br />

the pathogen<br />

Conclusions<br />

SEM <strong>of</strong> V. nonalfalfae conidia on<br />

E. brandti tarsal setae.<br />

E. brandti has potential <strong>of</strong> being an effective<br />

biological control agent<br />

<strong>Tree</strong>‐<strong>of</strong>‐<strong>heaven</strong> is the only species that can<br />

support E. brandti development from egg to<br />

adult<br />

E. brandti in combination with Verticillium<br />

nonalfalfae could be an effective control<br />

combination<br />

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Acknowledgments<br />

Scotty Bolling, Jackie Brown, and Ryan Mays at Virginia Tech, Dept.<br />

<strong>of</strong> Entomology<br />

Dr. Du Yu‐Zhou, Hailong Ji, and Yu Bo at Department <strong>of</strong> Plant<br />

Protection, Agricultural College, Yangzhou University, PRC<br />

Jennie McAvoy and Shicai Yan.<br />

Richard Reardon, USDA Forest Service ‐ FHTET<br />

These studies were supported by USDA Forest Service Grants<br />

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