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Appl Environ Microbiol, February 1998, p. 784-788, Vol. 64, No. 2
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Inactivation of Cryptosporidium parvum
Oocysts by Ammonia
Michael B.
Jenkins,1,*
Dwight D.
Bowman,2 and
William
C.
Ghiorse1
Section of Microbiology, Division of
Biological Sciences,1 and
Department of
Microbiology and Immunology, College of Veterinary
Medicine,2 Cornell University, Ithaca, New York
14853
Received 22 September 1997/Accepted 3 December 1997
 |
ABSTRACT |
The survival of Cryptosporidium parvum oocysts in soil
and water microhabitats may be affected by the environmental
production and release of free ammonia. The objective of this study was
to determine the effects of increasing free ammonia concentrations and
times of exposure on oocyst viability. Wild-type oocysts were obtained
from naturally infected calf feces by chemical (continuous-flow) centrifugation and sucrose gradients. Ammonia (NH3) from a
commercial solution was applied in concentrations ranging from 0.007 to
0.148 M. Exposure times ranged from 10 min to 24 h at a constant
temperature of 24 ± 1°C. Viability of oocysts was determined
with a dye permeability assay and an in vitro excystation assay
(M. B. Jenkins, L. J. Anguish, D. D. Bowman, M. J. Walker, and W. C. Ghiorse, Appl. Environ. Microbiol.
63:3844-3850, 1997). Even the lowest concentration of ammonia
decreased significantly the viability of oocysts after 24 h of
exposure. Increasing concentrations of ammonia increased inactivation
rates, which ranged from 0.014 to 0.066 h
1. At the
highest concentration of ammonia, a small fraction of viable oocysts
still remained. Exposure to pH levels corresponding to those associated
with the ammonia concentrations showed minimal effects of alkaline pH
alone on oocyst viability. This study shows that environmentally
relevant concentrations of free ammonia may significantly increase the
inactivation of oocysts in ammonia-containing environments.
 |
TEXT |
Unlike other common disinfectants,
ammonia is a natural product. It occurs in natural environments as a
product of urea hydrolysis and of the microbial degradation of proteins
and other nitrogen-containing compounds (referred to as
ammonification). Significant concentrations of ammonia may be
present in decomposing manure. Several studies have documented
NH3 evolution from cow manure during storage (7, 11-13, 19, 21, 22), even when the pH of the manure was <6.8 (13). The pH of NH3 evolving in manure generally
ranged from 7.5 (10) to 8.8 (7). Although
Cryptosporidium parvum oocysts can survive many months in
naturally infected manure under static conditions at 4°C
(9), inactivation may be enhanced under anaerobic conditions
in which ammonia persists. The objective of this study was to determine
the effects on inactivation of freshly purified oocysts of
environmentally relevant ammonia concentrations, ranging from 0.007 to
0.148 M, associated with manure slurries (22).
Oocyst purification.
Feces from 6- to 20-day-old Holstein
calves with cryptosporidiosis were processed by a continuous-flow
differential density flotation method, as described by Jenkins et al.
(9). Purified oocysts were adjusted to a concentration of
107 ml
1 and stored in distilled water
containing 100 U of penicillin G sodium ml
1, 100 µg of
streptomycin sulfate ml
1, and 0.25 µg of amphotericin B
ml
1 of oocyst suspension. The viability of each lot was
estimated with a fluorochrome dye permeability assay, and, for some
lots, in vitro excystation was performed as described below. Batches of
purified oocysts for all experiments ranged from 3 weeks to 4 months
old and ranged in viability from 90 to 95%.
Dye permeability assay.
The dye permeability assay, for
determining viability and potential infectivity of oocysts from
environmental water samples, has been described previously (1, 4,
9). Stock solutions of DAPI (4'-6-diamidino-2-phenylindole) (2 mg
ml
1 in high-performance liquid chromatography-grade
methanol) and propidium iodide (PI) (1 mg ml
1 in 0.1 M
phosphate-buffered saline [PBS]) were added to aliquots of the sample
in microcentrifuge tubes at a ratio of 1:10 (vol/vol); the sample was
then mixed with a Vortex mixer and incubated in the dark at 37°C for
2 h. Each aliquot was stained with Hydrofluor antibody (Hydrofluor
Combo; EnSys, Research Triangle Park, N.C.), washed twice with PBS,
and resuspended to the original volume in 0.3 M DABCO
(1,4-diazabicyclo[2.2.2]octane) in 0.1 M PBS (DABCO-PBS). The
samples were stored in the dark at 4°C until being examined (within
72 h).
In vitro excystation assay.
The acid pretreatment protocol was
described previously (9, 16). Each 100-µl aliquot of
oocyst suspension in microcentrifuge tubes was washed once with 1 ml of
acidified Hanks' balanced salt solution (HBSS) (10 µl of 1 M HCl in
10 ml of HBSS [pH 2.5]), resuspended in 1 ml of acidified HBSS, and
incubated at 37°C for 1 h in the dark. Suspensions were
then sedimented by centrifugation at 11,300 × g for
30 s; the pellets were washed three times with warm (37°C) HBSS
to remove any residual acid and then resuspended to 100 µl in warm
HBSS. Ten microliters of 2.2% sodium bicarbonate in HBSS and 10 µl
of 1% sodium deoxycholate in Hanks' minimal essential medium (Sigma
Chemical Co., St. Louis, Mo.) were added to each sample. The
suspensions were then mixed on a Vortex mixer and incubated for
3.5 h at 37°C in the dark. Ten microliters of primary Hydrofluor
antibody was then added to each sample, and they were mixed on a Vortex
mixer and returned to the incubator for 0.5 h, for a total
excystation incubation time of 4 h. The samples were then washed
in 1 ml of PBS, resuspended in 100 µl of PBS, and stained with 10 µl of Hydrofluor labeling reagent. After incubating at room
temperature in the dark for 0.5 h, oocysts were washed with 1 ml
of DABCO-PBS, suspended in 100 µl of DABCO-PBS, and stored at 4°C
until being examined (within 72 h). The percentage of excysted
oocysts was determined by subtracting the number of empty oocysts
observed before excystation from the number of oocysts observed after
excystation (9).
Microscopy.
All samples were examined with a Zeiss LSM-210
microscope (1) in conventional DIC and epifluorescence mode
with a triple excitation-emission filter set (catalog no. 61001; Chroma
Technology Corp., Brattleboro, Vt.) with excitations at 390 to 410, 485 to 510, and 555 to 585 nm and emissions at 450 to 475, 510 to 550, and
595 to 660 nm and a separate UV filter combination (excitation wavelength, 310 to 395 nm). Except for enumeration studies, a Zeiss
100×/1.3 plan-neofluor objective with 10× eyepieces was used for all
other microscopy.
Experimental design.
The source of ammonia for experimentation
was a commercial ammonia solution containing distilled water and
ammonia. The NH3 concentration was proprietary and
therefore was not given. All treatments were in triplicate. Freshly
purified oocysts were suspended in distilled water at a concentration
to 107 ml
1. A 0.1-ml aliquot of the oocyst
suspension was pipetted into 1.5-ml microcentrifuge tubes. Additional
quantities of distilled water were added to the tubes and corresponded
to the ammonia dilutions used as treatments: 90, 50, 25, 10, 5, 1, and
0% (vol/vol). The total volume of oocyst suspension per tube was 1 ml.
The pH of each dilution was measured with a standard, calibrated
calomel electrode, and the total NH4 concentration was
determined by the automated phenate method at the Soil Testing
Laboratory of Cornell University. The concentrations of NH3
were calculated for each dilution with the equation pOH = pKb + log
([NH4]/[NH3]) (6), where
Kb is the base dissociation constant. In
descending order, final concentrations were 0.148 M (2,516 mg/liter),
0.103 M (1,751 mg/liter), 0.060 M (1,020 mg/liter), 0.039 M (663 mg/liter), 0.026 M (443 mg/liter), and 0.007 M (119 mg/liter). The
tubes were incubated at room temperature (24 ± 1°C) in the
dark. The tubes were labeled so that analysis would be performed in a
blinded fashion. Tubes were sampled after 10 min, 1 h, and 24 h of incubation. The suspensions were washed four times in PBS and
resuspended in 0.1 ml of PBS. For each sampling time, one set of tubes
was assayed for viability with the dye permeability assay, and one set
underwent in vitro excystation. Two 10-µl subsamples per replicate
sample were observed microscopically, and 100 oocysts per subsample
were characterized.
To determine if the pHs of the ammonia solutions were the principle
factor in oocyst inactivation, freshly purified oocysts were also
exposed to three pH levels, 9, 10, and 11, which bridged the pHs of the
ammonia dilutions. A 0.01 M solution of CAPS
[3-(cyclohexylamino)-1-propanesulfonic acid] (Sigma) was adjusted
with either HCl or NaOH to obtain each pH level. Like the ammonia
experiments above, 107 oocysts suspended in 0.1 ml of
distilled water were pipetted into 1.5-ml microfuge tubes. One
milliliter of each CAPS solution was added. The tubes were mixed on a
Vortex mixer and incubated at 24 ± 1°C (room temperature).
Duplicate tubes were sampled at 10 min, 1 h, and 24 h. Both
the dye permeability assay and in vitro excystation were used to assess
viability, as described above. Oocysts suspended in PBS, pH 7.2, were
used as controls.
To validate the rates of oocyst inactivation as determined by the
results of the dye permeability assay (see Table 1), purified oocysts
were exposed (as described above) to an NH3 concentration of 0.060 M for 8.2 days, the projected time to reach 99.999%
inactivation (see Table 1). This concentration of NH3 was
chosen in order to compare our results with a claim made by Ruxton
(18). To determine if temperature is a factor in oocyst
inactivation by NH3, one set of replicate samples
(including controls) was incubated at 24 ± 1°C, and another set
was incubated at 4°C.
Statistical analysis.
Except where otherwise stated, all
statistical analyses of data were performed with Minitab Statistical
Software (Minitab Inc., State College, Pa.).
Effect of ammonia.
Based on the dye permeability assay, both
increased time of exposure and the concentration of ammonia increased
the inactivation rate of wild-type oocysts. Compared to the 1-h and
24-h exposure times, the 10-min exposure to the various concentrations
showed the greatest discrepancies between the dye permeability assay and in vitro excystation, the results of which appeared not to be as
time dependent as those of the dye permeability assay (Fig. 1). One-hour exposure showed better
agreement, and 24-h exposure showed the best agreement, between the two
assays. As previously observed (9), the dye permeability
assay generally indicated a slightly higher survival rate than in vitro
excystation. Results of the dye permeability assay indicated that
exposure to all ammonia concentrations increased oocyst wall
permeability (Fig. 2). The 10-min
exposure showed generally increased frequencies of DAPI-positive, PI-negative (DAPI+ PI
) oocysts with increased ammonia concentrations. Increased time of exposure resulted in increased frequencies of both
DAPI+ PI
and DAPI+ PI+ oocysts. After 1-h exposure, the frequency of
DAPI+ PI
oocysts appeared to reach a maximum between 24 and 36%,
after which the frequency of DAPI+ PI+ oocysts increased. A 24-h
exposure to 0.007 M ammonia at room temperature affected the
permeability of the oocyst wall in more than 50% of the purified population; the proportion of DAPI+ PI+ (nonviable) oocysts was slightly less than the proportion of DAPI+ PI
(potentially viable and/or infective) oocysts (Fig. 2). The progression of increased permeability of the oocyst wall from impermeable (DAPI
PI
) to partially permeable (DAPI+ PI
) to lethally permeable (DAPI+ PI+) has
been reported previously in relationship to increasing temperatures (9). The data indicated that increased times of exposure to the lowest concentrations of ammonia led to increases in the frequency of inactive (DAPI+ PI+) oocysts. Exposure to greater concentrations of
ammonia also increased the percentage of inactivated oocysts. With the
increased frequency of these inactivated oocysts, the correspondence
between viability, as determined by the dye permeability assay
(9), and the frequency of excysted oocysts, as determined by
the in vitro excystation assay, increased. The principle difference between the two viability assays at the 1-h exposure was attributable to the number of partially permeable (DAPI+ PI
) oocysts, which are
considered viable and potentially infective (1, 4, 9). Untreated oocyst controls that paralleled these experiments showed no
significant increase in oocyst wall permeability under the same
conditions of time and temperature.

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FIG. 1.
Viability of C. parvum oocysts exposed for 10 min, 1 h, and 24 h at 24 ± 1°C to various
concentrations of ammonia (0.007, 0.026, 0.039, 0.060, 0.104, and 0.148 M), based on the dye permeability assay and in vitro excystation. The
sum of the impermeable (DAPI PI ) and semipermeable (DAPI+ PI )
oocysts was the number of viable oocysts (9). Each datum
point represents the mean ± standard error (SE) of at least six
replicates of 100 oocysts observed per replicate. SE values not
indicated are smaller than the symbols. , viable; , excysted.
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FIG. 2.
Dynamics of dye permeability of oocysts as determined by
the dye permeability assay. Each point corresponds to, and is from the
same experiments as, the viability determinations of oocysts exposed to
various concentrations of ammonia for 10 min, 1 h, and 24 h
at 24 ± 1°C. Each datum point represents the mean ± standard error (SE) of at least six replicates of 100 oocysts observed
per replicate. SE values not indicated are smaller than the symbols.
, DAPI PI ; , DAPI+ PI ; , DAPI+ PI+; , empty.
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|
Based on the results of the dye permeability assay for each ammonia
concentration, rates of oocyst inactivation were determined by using a
first-order kinetic model (Table 1). With
the determination of these inactivation rates (K values) for
each ammonia concentration, the time it took to reach 99.999%
inactivation was calculated (Table 1). Regression analysis of the
ammonia concentration against the number of days required to reach
99.999% inactivation led to a power function that best fit
(r2 = 0.998) the regressed data. This power
function (Table 1) indicated that it would take an ammonia
concentration of 3.9 M to inactivate 99.999% of the freshly purified
oocysts in 24 h.
Effect of high pH on oocyst viability.
As indicated by the
increased frequency of DAPI+ PI
oocysts, there was a change in the
permeability status of the oocyst wall with increasing pH (Fig.
3). However, there was only minor change
in viability status, as indicated by the minimal change in frequency of
DAPI+ PI+ oocysts. The in vitro excystation assay also showed little
significant change in percent excystation with increasing pH (Fig.
4). These data strongly suggest that the
high pH levels associated with ammonia solutions may have primarily time-dependent effects on oocyst wall permeability, whereas free ammonia, which has previously been reported to be lipid soluble and
able to penetrate biological membranes (17), is able to permeate immediately the oocyst wall and sporozoite membranes and
inactivate the sporozoites and/or enzymes involved in excystation. Based on the model proposed by Robin (17), the equilibrium
equation NH3
NH4+
(6), and the nonpolar nature of NH3, we
hypothesize that an increased interoocyst NH3 concentration
raises the internal pH of the oocyst to deleterious levels. Because the
components of pH, viz. H+ and OH
, are
charged, they remain external to the oocyst wall, thus explaining the
inability of pH alone to inactive oocysts. The differential action of
the elevated pH and free ammonia concentration on the oocyst may
account for the initial differences (i.e., at 10-min exposure) between
the dye permeability assay and in vitro excystation (Fig. 1). Increased
oocyst wall permeability at elevated pHs associated with ammonia
production would also lead to increased susceptibility to other forms
of inactivation or disinfecting agents (15).

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FIG. 3.
Results of the dye permeability assay on oocysts exposed
to various pH levels (7, 9, 10, and 11) corresponding to the various
concentrations of ammonia and incubated at 24 ± 1°C for 24 h. The sampling scheme and statistical analysis were the same as
described in the legend to Fig. 1. , DAPI PI ; , DAPI+ PI ;
, DAPI+ PI+.
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FIG. 4.
Results of the dye permeability (A) and in vitro
excystation (B) assays on oocysts exposed to various pH levels (7, 9, 10, and 11, corresponding to the various concentrations of ammonia) and
incubated at 24 ± 1°C for 10 min, 1 h, and 24 h. The
sampling scheme and statistical analysis were the same as described in
the legend to Fig. 1. Squares, pH 7; diamonds, pH 9; circles, pH 10;
triangles, pH 11.
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Our results demonstrate that exposure to low concentrations of free
ammonia in solution can have a deleterious effect on the survival of
C. parvum oocysts. Fayer et al. (8) reported that oocysts suspended in water that were exposed to an atmosphere of pure
ammonia at room temperature (21 to 23°C) for 24 h were totally
inactivated, based on animal infectivity assays. At room temperature,
the solubility of gaseous ammonia is 32% (wt/wt) (10) or
~17.8 M. Two previous studies demonstrated the lethal effects of a
5% solution of Parsons' Ammonia (Armour-Dial) (~0.04 M) on oocyst
viability (5, 20). Ransome et al. (14) reported that a 1-h exposure at 10°C to 0.008 M ammonia resulted in an 85.6%
reduction in in vitro excystation compared to a control (excystation
rate not stated), and Blewett (2) reported that a 30-min
exposure at 22°C to a 0.009 M solution of ammonia reduced excystation
by 55%; both of these reductions in excystation were greater than the
reductions in excystation that we observed for 0.007 M and 0.026 M
NH3 at 24°C for 24 h (Fig. 1). Ruxton
(18) reported unpublished data suggesting that a 24-h
exposure to a 0.1% solution (0.06 M) would completely inactivate
oocysts. Our results showed that a 24-h exposure to 0.06 M ammonia
inactivated between 64.5% (based on the dye permeability assay) and
83.7% (based on in vitro excystation) of the oocysts. Based on our
kinetic analysis, exposure to 0.060 M ammonia would inactivate 99.999% of the freshly purified oocysts in 8.2 days (Table 1).
The data in Table 2 validated the
inactivation rate coefficient (K) at an NH3
concentration of 0.060 M and at a constant temperature of 24 ± 1°C; the calculated K value based on these data is 0.043 h
1, which is within the 95% confidence interval as
indicated in Table 1. The rate of inactivation for oocysts exposed to
0.060 M NH3 at 4°C was significantly less, however, at
0.0087 h
1, a K value that indicates a
hypothetical 26.5 days to reach 99.999% inactivation. These data
indicate that temperature is a significant factor in the inactivation
of oocysts by NH3, confirming the broad generalization that
temperature is an important environmental factor affecting oocyst
permeability (9). It further supports previous observations
that temperature affects the permeability of the oocyst wall; at
temperatures near freezing (4°C), oocysts are more impermeable to
solutes like nonpolar NH3 than at higher temperatures. The
viability of the controls was not significantly different from one
another or from the viability of the batch at time zero (90.8).
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TABLE 2.
Validation experiment showing the results of the dye
permeability assay on purified C. parvum oocysts exposed
to 0.060 M NH3 for 8.2 days
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|
Previous studies did not report on temperature affecting the
effectiveness of ammonia to inactivate Cryptosporidium
oocysts (2, 3, 8, 14, 20). The data in Table 2 indicate explicitly that oocysts exposed to NH3 at temperatures
around 25°C will be inactivated more quickly than at temperatures
close to freezing. Manure piles, for example, can warm up to 30°C and then, as in winter, cool to an ambient atmospheric temperature of 5°C
(9a), thus changing the effectiveness of NH3 on
the inactivation of oocysts.
Many municipal watersheds contain non-point sources of C. parvum oocysts, such as dairies. Neonatal calves are very commonly infected with C. parvum, and a single infected calf can shed
a few billion oocysts in the few days of its infection. Several studies
have indicated that the nitrogen content of cow manure is lost to the
atmosphere as gaseous ammonia (3, 7, 11, 12, 19). Although
loss of nitrogen as gaseous ammonia has been considered a loss of an
important plant nutrient, the evolution of ammonia in barnyard manure
may be used to inactivate C. parvum oocysts, as suggested by
Ruxton (18). Whitehead and Raistrick (22)
reported an increase of ammonia in a slurry of cattle manure over a
3-week period, from an initial concentration of 0.05 M to >0.2 M. Based on our results, exposure to such concentrations of ammonia would
significantly reduce the number of viable oocysts even at cool
temperatures, given longer times of exposure.
Although the concentration of ammonia is pH dependent, our study shows
that the pH associated with various concentrations of ammonia was not a
factor in oocyst inactivation but rather tended to affect the
permeability of oocyst walls, thus suggesting an indirect effect of pH
on oocyst wall permeability. It appears to be the chemical activity of
free ammonia, and its ability to penetrate the oocyst wall and
sporozoite membranes, that leads directly to oocyst inactivation.
 |
ACKNOWLEDGMENTS |
This research was supported in part by the Center for Advanced
Technology, sponsored by the New York State Science and Technology Foundation.
We are grateful to M. Frongillo and K. Wallace for purifying oocysts
and to L. Anthony for laboratory assistance. The expert secretarial
assistance of Patti Durfey is gratefully acknowledged.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Section of
Microbiology, Division of Biological Sciences, Wing Hall, Cornell
University, Ithaca, NY 14853. Phone: (607) 254-5117. Fax: (607)
255-3904. E-mail: mbj1{at}cornell.edu.
 |
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Appl Environ Microbiol, February 1998, p. 784-788, Vol. 64, No. 2
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
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