Postharvest Biology and Technology 83 (2013) 22–26
Contents lists available at SciVerse ScienceDirect
Postharvest Biology and Technology
journal homepage: www.elsevier.com/locate/postharvbio
Germination of fungal conidia after exposure to low concentration
ozone atmospheres
a b c,∗
Zilfina Rubio Ames , Erica Feliziani , Joseph L. Smilanick
a
Kearney Agricultural Center, University of California, 9240 South Riverbend Avenue, Parlier, CA 93648, USA
b
Department of Environmental and Crop Science, Marche Polytechnic University, Via Brecce Bianche, 60131 Ancona, Italy
c
USDA-ARS San Joaquin Valley Agricultural Sciences Center, 9611 South Riverbend Avenue, Parlier, CA 93648, USA
a r t i c l e i n f o a b s t r a c t
Article history: The germinability of conidia of Alternaria alternata, Aspergillus flavus, Aspergillus niger, Penicillium dig-
Received 13 July 2012
itatum, Penicillium expansum, or Penicillium italicum was determined periodically during exposure for
Accepted 11 March 2013 ◦
approximately 100 d to a humid atmosphere of air alone or with 150 nL/L ozone at 2 C. Conidia were
exposed on glass coverslips that were removed from chambers at intervals of one week and the ger-
Keywords:
mination of 100 conidia of each species was assessed after incubation for 24 h on potato dextrose agar.
Ozone
The period in d when 50% or 95% (ET50 and ET95, respectively) could not germinate and 95% confidence
Alternaria alternata
intervals for these estimates were made using Finney’s probit analysis. ET50 and ET95 estimates were
Aspergillus flavus
approximately one month and two to three months, respectively. Some natural mortality of the conidia
Aspergillus niger
occurred during these periods, so the entire decline in germinability was not solely due to ozone. The
Penicillium digitatum
Penicillium expansum age of the culture from which conidia were collected influenced their susceptibility to ozone. Conidia
Penicillium italicum were harvested from 7, 14, 21, and 28 d old potato dextrose agar cultures of P. digitatum and exposed to
◦
13,000 nL/L ozone at 2 C. After 48 h of exposure to ozone, none of the conidia from the seven-day old
culture germinated, while 30–35% of conidia from 14, 21, or 28 d in age cultures germinated.
Published by Elsevier B.V.
1. Introduction decay lesions caused by Penicillium spp. (Metzger et al., 2007; Palou
et al., 2003). Nothing about the mortality of the conidia of the citrus
Postharvest decay pathogens of fresh fruit and vegetables are pathogens was reported.
primarily filamentous fungi that reproduce by the production of In vitro studies revealed that ozone treatment suppressed
air borne conidia. The constant use of ozone in low concentrations the germination of conidia, with the degree of inhibitory action
during storage has been evaluated and showed some promise to dependent on the concentration and duration of exposure to ozone
extend storage life of several products by the control of these fungi (Tzortzakis et al., 2007). However, reports defining ozone doses that
(Karaca and Velioglu, 2007; Palou et al., 2006; Smilanick et al., 2012; kill conidia of postharvest fungal pathogens are few, their find-
Tiwari and Muthukumarappan, 2012). Sanitation of fruit surfaces ings vary widely, and few were conducted at cold temperatures
with ozone in air has been reported, but doses of ozone that kill and under humid conditions (Palou et al., 2006). Relative humidity
postharvest decay fungi in a few hours are very high (Ozkan et al., has a large effect on the sensitivity of conidia to ozone gas. Ozkan
2011), and to use them requires very ozone-tolerant commodi- et al. (2011) reported the concentration of ozone that killed 99%
ties because of the high risk of phytotoxicity. Ozone is harmful to of the conidia of Penicillium digitatum in 1 h decreased markedly,
humans if even brief exposure occurs to these high concentrations from 11,410 to 817 L/L (parts per million), when the humidity
(Rice, 2012), so the use of constant, low concentrations of 100 to was increased from 35 to 95%. Tzortzakis et al. (2007) reported
◦
300 nL/L (parts per billion) is used to reduce this hazard to workers exposure to a constant concentration of 200 nL/L ozone at 13 C and
and the size of the ozone generation equipment needed. Storage 95% relative humidity reduced viability of conidia of Colletotrichum
under ozone gas at a concentration of 300 nL/L reduced or delayed coccodes by more than 90% after eight hours, while this concentra-
the natural decay of a variety of citrus fruit, destroyed ethylene in tion had no effect on germinability of conidia of Alternaria alternata
the storage room air, and retarded the production of conidia from after up to 72 h, the longest exposure evaluated. This concentration
of ozone reduced conidial production of A. alternata by about 50%
after 10–14 d, while that of C. coccodes was unchanged. Antony-
∗ Babu and Singleton (2009) compared the influence of a sustained
Corresponding author. Tel.: +1 559 596 2810; fax: +1 559 596 2777.
ozone atmosphere (200 nL/L) on the growth, sporulation, and via-
E-mail addresses: [email protected], [email protected]
(J.L. Smilanick). bility of conidia of Aspergillus nidulans and Aspergillus orchraceus at
0925-5214/$ – see front matter. Published by Elsevier B.V. http://dx.doi.org/10.1016/j.postharvbio.2013.03.008
Z.R. Ames et al. / Postharvest Biology and Technology 83 (2013) 22–26 23
◦
18 C. A. nidulans cultured in ozone did not produce conidia, while Fremont, CA) and into a nurse tank (42.6 L), then into a distribution
A. orcharceus did, although at a much lower rate than in air. This manifold with needle valves and flow meters that independently
concentration caused a reduction in conidial germination of both controlled the rate of flow into a stainless steel chamber (116.8 L).
species by about 15% after 8 d. The gas stream was humidified by passage through water before it
Our goal was to determine the influence of ozone gas at a entered the chamber, and the high humidity (approximately 95%
constant concentration of 150 nL/L on the germinability of coni- RH) inside the chamber was confirmed with an electronic relative
dia of A. alternata, Aspergillus flavus, Aspergillus niger, P. digitatum, humidity sensor (Acurite model 359). Ozone concentration was
◦
Penicillium expansum, or Penicillium italicum at 2 C under humid confirmed and monitored every 30 min with a UV ozone moni-
conditions. In a second study, we evaluated the effect of colony age tor (Model 465, Advanced Pollution Instrumentation Systems, San
on the sensitivity of conidia of P. digitatum to ozone at a higher Diego, CA).
concentration (13,000 nL/L).
2.3. Germination of conidia
2. Materials and methods
Following exposure to air or ozone, the cover glasses were
2.1. Culture and preparation of conidia placed in a previously sterilized glass test tube. A volume of 100 L
of Triton X-100 was added and the tube was vortexed for 10 s.
P. digitatum and P. italicum were isolated from infected lemons, Aliquots of 10 L of the conidial suspension were plated on PDA,
Penicillium expansum from an infected apple, and A. flavus, A. niger, the conidial suspension dried on the PDA surface, the dishes were
◦
and A. alternata from contaminated almonds. All isolates originated closed and incubated for 18 to 24 h at 25 C, then 100 conidia were
from colonies initiated by a single-conidium and they were stored examined with a light microscope and the number of germinated
on silica gel. All were cultured on potato dextrose agar (Difco Lab- conidia were recorded.
oratories, Detroit, MI) for 2 weeks in a cycle consisting of 12 h
◦
in light (cool white fluorescent) and 12 h in darkness at 20 C.
2.4. Statistical analysis
In experiments where the influence of colony age on the sensi-
tivity of conidia of P. digitatum to ozone gas was examined, the
The time when 50% and 95% mortality was estimated with 95%
fungus was cultured for 7, 14, 21, or 28 d before conidia were har-
confidence intervals was determined using Finney’s probit analysis
vested. Conidia were rubbed from the media surface with a glass
(Finney, 1971; SPSS ver. 20, IBM Corporation, Armonk, NY) applied
rod after adding 2 mL of Triton X-100 (0.1% w/v). Conidia were fil-
to the number of conidia that could germinate, the total number
tered through at two layers of cheese cloth to remove mycelial
examined, and the time in hours or d of exposure to air or ozone.
fragments. A volume of approximately 0.1 mL of dense (approx-
−7 Germination data from two experiments were used.
imately 10 conidia/mL) suspensions of conidia were dispersed
onto one side of a cover glass (18 mm × 18 mm, Corning Inc., Corn-
ing, NY, USA) with a compressed air sprayer (model DB-32, Paasche 3. Results
5
Airbrush Co., Harwood Heights, IL) operating at 2.8 × 10 Pa to dis-
tribute the conidia evenly over the entire surface. Conidia were 3.1. Conidial germination after exposure to air or ozone
mostly deposited in a single layer and clumping of conidia was
minimal. Two identical 150 mm × 15 mm Petri dishes (Fisher Sci- The mortality of conidia in the low ozone concentration atmo-
entific, Pittsburgh, PA) with twenty cover glasses per fungus were sphere was slow and began after two to three weeks of ozone
prepared. The plates, without lids, were inverted and placed in exposure (Fig. 1). None of the conidia exposed to 150 nL/L ozone
◦ ◦
the ozone or air (control) atmospheres at 2 C and high humidity at 2 C for 100 d could germinate. The rank of ozone tolerance,
(approximately 95% RH) that was measured with an electronic rel- as determined the ET50 values, with the most tolerant stated first,
ative humidity sensor (Acurite model 359, Chaney Instrument Co., were A. flavus > P. italicum > A. niger > P. expansum > P. digitatum > A.
Lake Geneva, WI). All experiments were repeated twice. alternata (Table 1). The ranks of ozone tolerance, as determined
the ET95 values, with the most tolerant stated first, were A. alter-
nata > A. flavus > P. italicum > A. niger > P. expansum > P. digitatum.
2.2. Ozone system
Some reduction in germination also occurred in air, but a large per-
centage of the conidia exposed to air could germinate at the end of
Two ozone systems were used. For the long-term exposure of
the experiment. After exposure to air for 100 d, conidia of P. digita-
the conidia to a relatively low concentration of ozone (150 nL/L
tum, A. alternata, and A. niger declined to about 50% of their initial
or 150 parts per billion), a commercial corona discharge ozone
germination percentages, while germination of the conidia of P.
generator system (model 4900, Purfresh, Inc., Fremont, CA) was
italicum, P. expansum, and A. flavus was about 80% of their initial
installed on an environmental chamber. The generator concen-
percentages (Fig. 1).
trated oxygen from air, dried the air, passed it through an air-cooled
corona plates, and passed the ozone gas through Teflon lines to the
ozonated chamber. The dry oxygen produced by the system that 3.2. Influence of culture age on conidial sensitivity to ozone
was passed into the corona plates reduced the production of inter-
fering nitrogen radicals and nitric acid (Tapp and Rice, 2012). Ozone The age of the culture influenced the sensitivity of conidia to
concentration was monitored with an electrochemical detector ozone; conidia from colonies cultured for 7-day old cultures were
that controlled the ozone generator output. Ozone concentrations markedly more sensitive to ozone than those from older cultures
◦
were confirmed and monitored weekly with a UV ozone moni- (Fig. 2). After 24 h of exposure to ozone at 13,000 nL/L at 2 C ger-
tor (Model 465, Advanced Pollution Instrumentation Systems, San mination of conidia from the 7-day old culture declined to 20%,
Diego, CA). For the short term exposure of conidia to a relatively while those from the 14-, 21-, and 28-day old cultures germinated
high concentration of ozone (13,000 nL/L or 13 parts per million), at 40, 70, and 60%, respectively. After 48 h of exposure to ozone,
air was dried by passage through a 1.4-m long by 6 cm wide column none of the conidia from the 7-day old culture could germinate,
filled with anhydrous calcium sulfate (W.A. Hammond Drierite Co., while 30–35% of the conidia from cultures 14, 21, or 28 d in age
Xenia, OH), passed through a corona discharge generator (Purfresh, germinated. None could germinate after 72 h exposure to ozone.
24 Z.R. Ames et al. / Postharvest Biology and Technology 83 (2013) 22–26
Fig. 1. Germination of conidia of Alternaria alternata, Aspergillus flavus, Aspergillus niger, Penicillium digitatum, Penicillium expansum, or Penicillium italicum after exposure in
◦
d to atmospheres of air () or 150 nL/L ozone () at 2 C.
Table 1
Germinability of conidia of Alternaria alternata, Aspergillus flavus, Aspergillus niger, Penicillium digitatum, Penicillium expansum, or Penicillium italicum after exposure in days
◦
to an atmosphere of 150 nL/L ozone at 2 C.
a
Fungus Days in ozone at 150 nL/L
ET50 (±95% CI) ET95 (±95% CI)
Alternaria alternata 18.7 (14.0, 22.3) 107.3 (99.3, 117.3)
Aspergillus flavus 43.9 (41.5, 46.3) 86.8 (82.4, 92.0)
Aspergillus niger 36.2 (29.4, 42.9) 74.5 (64.3, 91.1)
Penicillium digitatum 21.7 (21.1, 30.7) 54.0 (46.2, 67.2)
Penicillium expansum 23.0 (18.4, 27.3) 69.5 (62.4, 79.1)
Penicillium italicum 42.9 (38.8, 47.0) 79.4 (72.7, 88.3)
a
Values indicate the period in d when 50% (ET50) or 95% (ET95) of the conidia could not germinate, followed by the 95% confidence interval (CI). Values were estimated
using Finney’s probit analysis. Conidia, exposed to ozone on cover glasses, were removed from the ozone chamber at intervals of one week and the germination of 100 conidia
was assessed after incubation for 24 h on potato dextrose agar.
The germination of conidia after exposure to air for these periods Low concentrations of ozone gas have been applied to oxidize
was unchanged. ethylene gas to retard the accelerated ripening it causes, to reduce
worker exposure to ozone and the risk of phytotoxicity or other
harm to treated products, to minimize corrosiveness to rooms and
4. Discussion refrigeration coils compared to that caused by very high concentra-
tions of ozone or sulfur dioxide, and to facilitate the use of smaller
The germinability of conidia of the fungi exposed to constant ozone generators to reduce capital and operating costs (Palou et al.,
◦
low concentrations of ozone at 2 C with high humidity declined 2006). It has been amply demonstrated that ozone at low concen-
over a period of weeks; complete mortality did not occur until trations will alter, and usually decrease, the conidial production of
after two months or more. These results predict the rate of mor- many fungi (Antony-Babu and Singleton, 2009; Palou et al., 2002;
tality that could be expected to occur when ozone is used at low Tzortzakis et al., 2008). This is one of few studies that examined the
concentrations during the storage of horticultural products. rates of conidial mortality of common postharvest decay pathogens
Z.R. Ames et al. / Postharvest Biology and Technology 83 (2013) 22–26 25
of culture age on the sensitivity of A. niger and A. flavus to ozone gas.
Cultures of A. flavus became increasingly tolerant to ozone from
age 3 d to 9 d, while those of A. niger were unchanged and equally
sensitive at these ages.
5. Conclusions
Conidia of A. alternata, A. flavus, A. niger, P. digitatum, P. expansum,
or P. italicum were exposed to ozone gas at 150 nL/L for 100 d at
◦
2 C. In the ozone atmosphere, about 50% of the conidia did not
germinate after 3–4 weeks, while 95% did not germinate after 2–3
months. In air, some mortality also occurred during these periods,
but 50% or more was alive after 3 months. It is probable that the
mode of action of low concentrations of ozone applied to control
fungi on stored products is not mortality of their conidia. Conidia
from older colonies of P. digitatum were more tolerant to ozone
than those from younger colonies.
Fig. 2. Influence of the age of the culture of Penicillium digitatum on the susceptibility
◦
of conidia to inhibition by 13,000 nL/L of ozone gas at 2 C.
Acknowledgements
We thank Kent Fjeld for the design, fabrication, and opera-
under conditions similar to those of commercial storage. Because tion of the high concentration ozone system, Dennis Margosan
mortality of conidia occurs relatively slowly, it is likely mortal- for help with cultures and germination assays, financial support
ity of conidia alone is not the principle mechanism of ozone to of California Citrus Research Board and California Table Grape
control diseases caused by these fungi. In studies that reported Commission, Ozone International for loan of equipment and its
benefits in storage life resulting from the use of ozone gas, sec- maintenance, Luciana Cerioni for her technical help, and Mary Lu
ondary effects (Palou et al., 2003; Metzger et al., 2007), such as Arpaia for administrative support.
retarded senescence of fruit or vegetables in storage caused by
the control of ethylene, a reduction in air-borne inoculum within
References
storage rooms caused by the suppression of conidial production,
reduced aerial mycelia growth and associated spread among pro-
Antony-Babu, S., Singleton, I., 2009. Effect of ozone on spore germination, spore
duce after harvest, or induction of pathogen resistance in the hosts, production and biomass production in two Aspergillus species. Antonie van
Leeuwenhoek 96, 413–422.
are likely to of greater importance than mortality of conidia of
pathogens. Feliziani, E., Fjeld, K., Romanazzi, G., Smilanick, J.L., 2012. Continuous ozone concen-
trations during cold storage to control postharvest gray mold in grapes, 2011.
It is interesting that ozone controls postharvest decay caused Plant Dis. Manage. Rep. 6, SMF010.
by Botrytis cinerea at concentrations that are only a fraction of the Finney, D.J., 1971. Probit Analysis. Cambridge University Press, Boston, MA.
Hildebrand, P.D., Forney, C.F., Song, J., Fan, L., McRae, K.B., 2008. Effect of a contin-
more than 700 L/L that killed conidia in a 1-h exposure (Ozkan
uous low ozone exposure (50 nL L−1) on decay and quality of stored carrots.
et al., 2011). Palou and coworkers (2002) observed that an atmo-
Postharvest Biol. Technol. 49, 397–402.
sphere of 300 nL/L of ozone stopped mycelial growth and spread Karaca, H., Velioglu, Y.S., 2007. Ozone applications in fruit and vegetable processing.
Food Rev. Int. 23, 91–106.
of B. cinerea among table grapes, but infections by conidia on the
Metzger, C., Barnes, J.D., Singleton, I., Andrew, P., 2007. Effect of low level ozone-
surface of the fruit were only slightly reduced in this atmosphere,
enrichment on the quality and condition of citrus fruit under semi-commercial
indicating mortality of conidia was not occurring. Feliziani and conditions. In: Proc. IOA Conference and Exhibition, Valencia, Spain, vol. 11, pp.
1–7.
coworkers (2012) reported ozone concentrations as low as 100 nL/L
Ozkan, R., Smilanick, J.L., Karabulut, A.O., 2011. Toxicity of ozone gas to conidia of
stopped aerial mycelial growth of B. cinerea. Observing the same
Penicillium italicum, and Botrytis cinerea and control of gray mold on table grapes.
pathogen on carrots, Hildebrand and coworkers (2008) noted its Postharvest Biol. Technol. 60, 47–51.
Palou, L., Crisosto, C.H., Smilanick, J.L., Adaskaveg, J.E., Zoffoli, J.P., 2002. Effects of
aerial spread markedly retarded by 50 nL/L ozone, with some reduc-
continuous 0.3 ppm ozone exposure on decay development and physiological
tion in lesion size. They also reported that the B. cinerea sporulation
responses of peaches and table grapes in cold storage. Postharvest Biol. Technol.
was stimulated on carrots by ozone, while the pathogen produced 24, 39–48.
Palou, L., Smilanick, J.L., Crisosto, C.H., Mansour, M., Plaza, P., 2003. Ozone gas pen-
aerial mycelial growth in air. We have observed similar phenomena
etration and control of the sporulation of Penicillum digitatum and Penicillium
on table grapes, where ozone at 100 nL/L or higher stimulated
italicum within commercial packages of oranges during cold storage. Crop Prot.
sporulation of B. cinerea and suppressed the development of aerial 22, 1131–1134.
mycelium (Feliziani et al., 2012). In air and darkness, B. cinerea Palou, L., Smilanick, J.L., Margosan, D.A., 2006. Ozone application for sanita-
tion and control of postharvest diseases of fresh fruits and vegetables. In:
sporulation is nearly absent (Reuveni et al., 1989); apparently, by
Troncoso-Rojas, R., Tiznado-Hernandez, M.E., Gonzales-Leon, A. (Eds.), Recent
inducing this mode of growth instead of aerial mycelial growth,
Advances in Alternative Postharvest Technologies to Control Fungal Dis-
nested spread typical of the pathogen among stored products was eases in Fruits & Vegetables. TransWorld Research Network, Kerala, India,
pp. 1–32.
retarded by ozone, while mortality of the conidia had no role. It is
Reuveni, R., Raviv, M., Bar, R., 1989. Sporulation of Botrytis cinerea as affected
interesting that ultraviolet light also induces B. cinerea sporulation
by photoselective polyethylene sheets and filters. Ann. Appl. Biol. 115,
(Reuveni et al., 1989). It is likely that components of the hyphae 417–424.
Rice, R.G., 2012. Health and safety aspects of ozone processing. In: O’Donnell,
that determine the mode of growth of this fungus are susceptible
C., Tiwari, B.K., Cullen, P.J., Rice, R.G. (Eds.), Ozone in Food Processing. Wiley-
to both photodegradation and ozonolysis.
Blackwell, West Sussex, England, pp. 265–288.
Colony and conidial age influence the sensitivity of conidia of Smilanick, J.L., Mlikota Gabler, F., Margosan, D.A., 2012. Evaluation under commer-
cial conditions of the application of continuous, low concentrations of ozone
P. digitatum to ozone. We found the sensitivity of the conidia to
during the cold storage of table grapes. ISHS Acta Hortic. 945, 357–361.
ozone declined when the age of the culture from which they were
Tapp, C., Rice, R.G., 2012. Generation and control of ozone. In: O’Donnell, C., Tiwari,
harvested increased. Although true with this pathogen, it may not B.K., Cullen, P.J., Rice, R.G. (Eds.), Ozone in Food Processing. Wiley-Blackwell,
West Sussex, England, pp. 33–54.
be so for others. Zotti and coworkers (2008) examined the influence
26 Z.R. Ames et al. / Postharvest Biology and Technology 83 (2013) 22–26
Tiwari, B.K., Muthukumarappan, K., 2012. Ozone in fruit and vegetable processing. Tzortzakis, N., Singleton, I., Barnes, J., 2008. Impact of low-level ozone-enrichment
In: O’Donnell, C., Tiwari, B.K., Cullen, P.J., Rice, R.G. (Eds.), Ozone in Food on black spot and anthracnose rot of tomato fruit. Postharvest Biol.Technol. 47,
Processing. Wiley-Blackwell, West Sussex, England, pp. 55–80. 1–9.
Tzortzakis, N., Singleton, I., Barnes, J., 2007. Deployment of low-level ozone- Zotti, M., Porro, R., Vizzini, A., Mariotti, M.G., 2008. Inactivation of Aspergillus spp.
enrichment for the preservation of chilled fresh produce. Postharvest Biol. by ozone treatment. Ozone Sci. Eng. 30, 423–430.
Technol. 43, 261–270.