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May 2010, Volume 94, Number 5
Page 634
http://dx.doi.org/10.1094/PDIS-94-5-0634C
Disease Notes
First Occurrence of Laurel
Wilt Disease Caused by
Raffaelea lauricola on Redbay
Trees in Mississippi
J. J. Riggins, Department of Entomology and Plant Pathology,
Mississippi State University, Mississippi State 39762; M. Hughes,
Department of Plant Pathology, University of Florida, Gainesville
32611; J. A. Smith, School of Forest Resources and Conservation,
University of Florida, Gainesville 32611; A. E. Mayfield, III,
USDA Forest Service Southern Research Station, Asheville, NC
28806; and B. Layton, C. Balbalian, and R. Campbell, Department
of Entomology and Plant Pathology, Mississippi State University,
Mississippi State 39762. Approved for publication as Article No.
A-11714 of the Mississippi Agricultural and Forestry Experiment
Station
Open Access.
Laurel wilt is a lethal, nonnative vascular wilt disease of redbay
(Persea borbonia), sassafras (Sassafras albidum), and other trees
in the Lauraceae (1,4). It is caused by a fungus (Raffaelea
lauricola) and transmitted by the redbay ambrosia beetle
(Xyleborus glabratus), a nonnative insect first detected in Georgia
in 2002 (1,2). Since introduction of the pathogen and vector
(presumably from Asia), laurel wilt has caused extensive mortality
to redbays in Georgia, Florida, and South Carolina (1). In June
2009, a landowner in Gautier, MS reported dead redbay trees.
Signs and symptoms were identical to those reported for laurel
wilt along the Atlantic Coast (wilted, bronze red foliage, and dark
gray-to-black vascular discoloration) (1). Infected trees have
subsequently been confirmed in and near the Pascagoula River
Basin. Size of infected redbays ranged from 5 to 20 cm (diameter
at breast height). No heavily decomposed or fallen redbays were
noted. Many individual specimens exhibited extensive drying of
stem wood and dry, wilted, light brown foliage. This indicates that
introduction to the area may have occurred within the last 3 years.
X. glabratus adults were collected (30°26′44.45″N,
88°39′41.83″W) in a Lindgren funnel trap baited with phoebe and
manuka oil lures. Beetle identification was confirmed by USDA-
APHIS, and voucher specimens were submitted to the
Smithsonian National Museum of Natural History and the
Mississippi Entomological Museum. Symptomatic redbay wood
chips from the same location were surface sterilized and plated on
cycloheximide-streptomycin malt agar and R. lauricola was
isolated. A 1,026-bp portion of 18S rDNA (GenBank No.
GQ996063) was amplified by PCR and sequenced using primers
NS1 and NS4. BLASTn searches revealed perfect homology to R.
lauricola isolate PL 697 (GQ329704). Two isolates of R. lauricola
were recovered and prepared into separate spore suspensions (1 ×
108 CFU/ml). Each isolate was inoculated into two healthy
redbays. The inoculated redbays were placed in a growth chamber
with two water-only controls. All inoculated plants, and none of
the controls, exhibited wilt symptoms and died within 20 days. R.
lauricola was recovered from the discolored sapwood of the
inoculated plants, completing Koch's postulates. A model
prediction for the natural dispersion of X. glabratus and R.
lauricola estimated that these organisms may not reach
Mississippi for 10 to 15 years (3). The current detection of laurel
wilt in Mississippi is substantially ahead of this estimate.
Currently, no records of laurel wilt have been reported from
western Georgia, all of Alabama, or the panhandle of Florida.
Confirmed locations in Mississippi are in Jackson County, along
the Interstate 10 corridor and the Pascagoula River drainage. Due
to the relatively large extent of the infestation (~64 km2, including
hundreds of infected trees) eradication is not being attempted.
Surveys, remote sensing, and phylogeographic analysis are
underway to delineate the extent of infestation and discover the
mode of introduction. The current outbreak of laurel wilt in
Mississippi is likely the result of human transport of infested
wood, either from Asia as a separate, new introduction or from
previously infested areas in the southeastern United States.
References: (1) S. W Fraedrich et al. Plant Dis. 92:215, 2008. (2)
T. C. Harrington et al. Mycotaxon 104:399, 2008. (3) F. Koch and
W. Smith. Environ. Entomol. 37:442, 2008. (4) J. A. Smith et al.
Plant Dis. 93:198, 2009.