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Atmospheric Environment 38 (2004) 651–655
Fungal spores are transported long distances in smoke from
biomass fires
Sarah A. Mims, Forrest M. Mims III*
Geronimo Creek Observatory, 433 Twin Oak Road, Seguin, TX 78155, USA
Received 1 October 2003; received in revised form 20 October 2003; accepted 22 October 2003
Abstract
Viable fungal spores are present in smoke from distant biomass fires. This finding has potentially important
implications for prescribed burning, agricultural management and public health. While attempting to find fungal spores
in dust blown from China to Texas, one of us (S.A.M.) discovered that smoke from Yucatan contains viable bacteria
and fungal spores, including the genera Alternaria, Cladosporium, Fusariella and Curvularia. There was a high
correlation (r2¼0:78) of spores and coarse carbon particles collected on microscope slides during 13 days of the 2002
smoke season. To eliminate possible contamination by local spores, an air sampler was flown from a kite at a Texas
Gulf Coast beach during and after the 2003 smoke season on days when the NOAA back trajectory showed air arriving
from Yucatan. Fifty-two spores and 19 coarse black carbon particles (>2.5 mm) were collected during a 30-min kite
flight on the smoke day and 12 spores and four carbons on the day without smoke. We have found spores in smoke
from an Arizona forest fire and in Asian smoke at Mauna Loa Observatory, Hawaii. We have tested these findings by
burning dried grass, leaves, twigs and flood detritus. The smoke from all test fires contained many spores.
r2003 Elsevier Ltd. All rights reserved.
Keywords: Prescribed fires; Agricultural fires; Public health; Carbon; Dust
1. Introduction
We have found that convection caused by biomass
fires can launch fungal spores and bacteria skyward,
where they may travel thousands of kilometers. While
the long-distance transport of fungal spores on currents
of air is well established (Meier and Lindbergh, 1935;
Brown and Hovmoller, 2002), we are unaware of a prior
publication that describes fire-induced convection as a
mechanism for initiating such long-distance transport.
Karnal bunt, a smut infection of wheat caused by
Tilletia indica, can spread by convection to surrounding
fields when diseased wheat is burned (Roux and
O’Brien, 2001). This disease has spread around the
world from its origin in India, and the findings reported
here suggest that fire-induced convection might spread
pathogenic spores much greater distances than sur-
rounding fields.
Sugarcane rust caused by the fungus Puccinia
melanocephala, appeared in the Dominican Republic in
July 1978. Purdy et al. (1985) suggest this outbreak
followed transoceanic transport of spores from West
Africa. Because sugarcane is burned at harvest, we
suggest that convection caused by fire could have
launched spores into the air stream that delivered
inoculum to the Caribbean. Burning of diseased plants
is so widespread, and often mandated, that there are
many similar scenarios for the launching of pathogenic
microbes by fire-induced convection.
There is an abundant literature on long-distance
transport of fungi that are pathogenic to plants and
that cause allergic reactions when inhaled by people
(Kendrick, 2000;Griffin et al., 2001;Brown and
Hovmoller, 2002). Microbes are unique among particulate
ARTICLE IN PRESS
*Corresponding author. Tel.: +1-830-372-0548; fax: +1-
830-372-2284.
E-mail address: forrest.mims@ieee.org (F.M. Mims III).
1352-2310/$ - see front matter r2003 Elsevier Ltd. All rights reserved.
doi:10.1016/j.atmosenv.2003.10.043
matter, for, unlike nonviable particles, microbes can
rapidly multiply. Thus, the transport of a small number
of pathogenic spores can result in the eventual infection
of entire fields. This phenomenon is well known and can
sometimes be forecast. For example, the North Amer-
ican Plant Disease Forecast Center at North Carolina
State University publishes on the Internet forward
trajectories of Pseudoperonospora cubensis, which causes
Downy mildew in squash, cucumbers, pumpkins, and
muskmelons, and Peronospora tabacina Adam, which
infects tobacco (Main et al., 2001). Similar forecasts
might be relevant to smoke events.
2. Fungal spores and Central American smoke
Fungal spores and bacteria are associated with dust
that originates in North Africa and reaches the
Caribbean. Griffin et al. (2001) discuss bacteria and
spores associated with Sahara dust transported across
the Atlantic. Shinn et al. (2000) describes how the soil
fungus Aspergillus in Sahara dust infects Caribbean
coral reefs. During a study in April 2002 to determine if
viable microbes are transported with dust transported
from Asia to Texas, one of us (S.A.M.) serendipitously
discovered many viable fungal spores and bacteria
associated with smoke arriving at Geronimo Creek
Observatory in South-Central Texas (29.6N, 97.9W)
from large fires in Yucatan, Mexico.
2.1. Central American smoke at Central Texas, 2002
During the April 2002 smoke event, the Navy Aerosol
Analysis and Prediction System (NAAPS) aerosol
forecast model (US Naval Research Observatory,
www.nrlmry.navy.mil/aerosol/) showed that the smoke
originating in Yucatan traveled some 1450 km and
reached Geronimo Creek Observatory in 2–3 days.
The smoke reduced visibility, increased the optical depth
measured by Sun photometers, created a pronounced
solar aureole, and caused sharp increases in the number
of 0.5 mm particles.
On 13 days during this event, a microscope slide was
placed on a 4-m meteorological tower in an open field to
collect coarse carbon particles (diameter >2.5 mm) and
spores. At local noon, two nutrient media films (3 M
Petrifilms (TM)), one formulated for bacteria (Petrifilm
Aerobic) and one for fungi (Petrifilm Yeast and Mold),
were hydrated with distilled water, exposed for 15 min
on the tower, and incubated 3 days at ambient
temperature.
Many colonies of fungi and bacteria grew on the films
exposed during the smoke episode. The microscope
slides permitted the numerical relationship of the spores
and coarse carbon particles in the smoke to be
quantified. Four scans across the width of each slide
were made, and all spores and coarse carbon particles
were counted. Fungal spores included representatives
from 22 genera, including Alternaria, Cladosporium,
Fusariella, Nigrospora, and Curvularia. As shown in
Fig. 1, the correlation of all coarse carbon particles and
spores deposited on slides during the smoke episode was
very high (r2¼0:78). However, the correlation of some
genera with carbon particles was very low (e.g., r2¼
0:00 and 0.05). These were likely local in origin.
2.2. Central American smoke at Texas Gulf Coast, 2003
Smoke from Yucatan again reached Texas during
May 2003. A passive air sampler designed by S.A.M.
was flown from a kite over a beach at North Padre
Island, Texas (27.4N, 97.3W), on days when smoke from
Yucatan was present and not present to eliminate
interference from spores originating in Texas. Fig. 2
summarizes the kite experiments.
On 3 May 2003 (Fig. 2a, c and d), NOAA back
trajectories showed that air at the Texas Gulf Coast had
passed over Yucatan 48 h earlier. Terra MODIS and
SeaWiFS imagery showed that smoke from fires in
Yucatan covered the Western Gulf of Mexico. During
the kite flight, a nearby monitoring station (CAMS 341)
operated by the Texas Commission on Environmental
Quality measured 16.1 mg/m
3
of PM 2.5 particles in air
arriving from over open water at a mean direction of
134. A 30-min flight captured 52 fungal spores and 19
coarse carbon particles (Fig. 2e).
On 5 August 2003, the NOAA back trajectory again
showed air coming from Yucatan. Terra MODIS
imagery showed no major fires in Yucatan and the
study site. During the kite flight, CAMS 341 measured
5.5 mg/m
3
of PM 2.5 particles in wind arriving from over
open water at a mean direction of 161. A 30-min flight
captured 12 fungal spores and four coarse carbon
particles (Fig. 2f).
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Fig. 1. Xy scattergraph (r2¼0:78) of fungal spores and coarse
carbon particles deposited by sedimentation on exposed
microscope slides at Geronimo Creek Observatory in South
Central Texas on all 13 days samples were collected from 25
April–10 May 2002 during a major Central American smoke
event.
S.A. Mims, F.M. Mims III / Atmospheric Environment 38 (2004) 651–655652
Spores collected by the kite sampler include many of
those collected during the 2002 Yucatan smoke event,
including the genera Alternaria, Cladosporium,Fusar-
iella and Curvularia. The kite study provides compelling
evidence that spores were present in smoke from
Yucatan arriving at the Texas Gulf Coast.
3. Fungal spores in other smoke events
We collected fungal spores in smoke from a forest fire
in Arizona (18 June 2003) and in smoke from Canada
and Louisiana at College Station, Texas (10 August
2003). We collected Alternaria and other spores and
carbon particles at Mauna Loa Observatory (MLO),
Hawaii (elevation 3400 m), during a rare Asian smoke
event (6 July 2003). The smoke formed distinct layers
and was associated with high concentrations of ozone
(>70 ppb), which were highly correlated (r2¼0:98)
with the 5 mm particle count.
4. Experimental validation of fungal spores in smoke
A simple experiment was designed to determine if
fungal spores and bacteria are present in smoke from
burning grass. Four Petrifilms (two bacteria and two
mold) were clipped to a horizontal pole and exposed to
smoke from burning grass for 5 min. A second set of
four Petrifilms was exposed to background air for 5 min.
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Fig. 2. On days when the NOAA back trajectory (a,b) indicated air arrived at North Padre Island, Texas, from Yucatan 48 h earlier
(4 May and 5 August 2003), an air sampler was flown from a kite at a Gulf Coast beach when smoke from Yucatan was present (c) and
not present (d). During 30-min flights, the sampler collected 52 spores and 19 coarse carbons on the smoke day (e), and only 12 spores
and four carbons on the nonsmoke day (f).
S.A. Mims, F.M. Mims III / Atmospheric Environment 38 (2004) 651–655 653
After 3 days of incubation at ambient temperature, the
films exposed to smoke had a total of >115 mold and
>90 bacteria colony forming units (CFUs). Those
exposed to background air had only 10 mold and eight
bacterial CFUs.
Various kinds of biomass were placed on a steel plate
in an open field and burned. Smoke from each fire was
sampled for 1 min using three Petrifilms (mold only).
The temperature of the films, which was monitored with
noncontact IR thermometry, ranged from 34Cto49
C.
Between fires, the background air was sampled for 1 min
using three Petrifilms. A wood walkway prevented
contamination by local spores. After 3 days of incuba-
tion at ambient temperature, nutrient films exposed to
smoke from all the biomass samples exhibited signifi-
cantly more CFUs than those exposed to ambient air
between burns. The ratios of total CFUs in smoke to
CFUs in background air were 9:3 (dry grass), 19:0 (dry
leaves), 48:4 (twigs) and 87:5 (flood detritus).
Our observations and photographs of test fires under
a plant canopy suggest that agitation of leaves caused by
turbulent convection (Pisaric, 2002) may dislodge
spores, which are then carried upward with the warm
plume. Nearer the ground, turbulent air rushing in to
feed the flames may also carry spores into the smoke
plume.
5. Conclusions
The common assumption that plant pathogens are
killed by burning is contradicted by the spread of Karnal
bunt to surrounding fields when wheat infected with T.
indica is burned (Roux and O’Brien, 2001). Our findings
of many fungal spores in smoke from all test fires, and
from large fires in Yucatan more than 1500 km distant,
suggest that plant pathogens might be spread consider-
ably farther than surrounding fields. Some fungal spores
we have found in smoke (e.g., Alternaria) cause allergic
reactions and trigger asthma attack (Kendrick, 2000).
Heretofore, such reactions have been attributed solely to
smoke inhalation, and we propose that fungal spores
may also play a role. We propose to test this hypothesis
by comparing emergency department visits for asthma
and allergy-related respiratory incidents with spore
counts by the Aeroallergen Monitoring Network of the
American Academy of Allergy, Asthma and Immunol-
ogy (Anon, 2001), which reveal examples of high mold
counts during smoke events. This study will also
examine incidence of asthma attack in the weeks after
major smoke events, for the progeny of spores
transported with smoke might be an even greater
problem.
Prescribed burns of diseased crops, brush, timber,
slash and rubbish may disperse large numbers of
pathogenic fungi. Major fires, which can produce smoke
plumes 3 km or more high, could be much more effective
in launching spores into the troposphere than surface
wind storms. Small burns of diseased plants and cooking
and heating with diseased firewood might disperse
pathogenic spores on a smaller scale.
A beneficial role for spores carried skyward with
forest fire smoke could be reinoculation of fire-sterilized
soil with mycorrhizal fungi and the dispersal of
such symbiotic fungi to new locations. We plan to
test this hypothesis. We also plan to study the
variety and number of spores and bacteria in smoke
from various kinds of fires. The abundance of spores
relative to coarse carbon particles, 3:1 for Yucatan
smoke in Texas and 1:1 for Asian smoke at MLO,
could have a slight influence on radiative transfer
models, for spores are regularly shaped and often
translucent, while coarse carbon is opaque, black and
irregularly shaped.
Acknowledgements
Tom Gill informed us that Central American smoke
was present when fungal spores were first found in
smoke. Mark Hartwig suggested the design hypothesis
that dispersal in smoke of mycorrhizal fungal spores
might be beneficial. John Barnes facilitated sampling at
Mauna Loa Observatory. Gabriel Solis and Ryan
Peschel assisted with test fires. Gerald Holmes informed
us about the spread of Karnal bunt by burning. We
thank those responsible for NOAA back trajectories,
GSFC MODIS imagery and the NRL NAAPS model.
We also thank Eugene Shinn for helpful discussions and
the editor and two anonymous reviewers for suggestions
that greatly improved the manuscript.
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