The commercially available Burkard cyclonic sampler takes in air volumetric
ally, creates a vortex in an aluminum cylinder, and deposits particulates i
n an Eppendorf vial. Retention within the cylinder was determined for ascos
pores released by cultures of Sordaria fimicola and Gibberella zeae. Manufa
cturer's recommended amperage level and reduced power were tested, and a su
rfactant was applied to the cylinder wall. Under recommended power, an aver
age of 78% of the S. fimicola ascospores were collected in the vial, while
22% lodged inside the cylinder. Conversely, only 25% of the G. zeae ascospo
res were collected in the vial, while 75% remained lodged inside the cylind
er. Application of a surfactant to reduce the adherence of ascospores on th
e cylinder wall, instead resulted in 83% of the S. fimicola ascospores and
99.7% of the G. zeae ascospores deposited on the cylinder wall. When the po
wer supply was decreased from 200 mA to 140 mA, the ratio of ascospores of
G. zeae retained by the sampler remained nearly the same, indicating that t
he retention error was not a function of airflow rate within the tested pow
er range. However, the total number of ascospores collected was significant
ly less under reduced power. A 90-A/h (12 V) battery supplied greater than
150 mA when connected to the Burkard for 4 days at temperatures between 22
and 28 degreesC and could maintain current above 190 mA for 7 days with a 2
1-W solar panel. A 21-W solar panel charging a 90-A/h battery should mainta
in the amperage needed for the Burkard to maintain proper flow rate in most
environments. The aluminum cylinder should be rinsed out thoroughly when c
ollecting samples of fungal ascospores or any other particulates with the p
ropensity to adhere to the cylinder wall.