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Applied and Environmental Microbiology, December 2005, p. 7974-7979, Vol. 71, No. 12
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.12.7974-7979.2005
USDA-ARS, U.S. Meat Animal Research Center, Clay Center, Nebraska
Received 5 May 2005/ Accepted 27 August 2005
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Beef animal production typically involves the concentration of animals in feedlot pens and the provision of energy-rich diets (grain and/or grain silage) to maximize animal performance. Manure collected from cattle operations is often stored and later applied to the land as a means of disposal as well as a source of nutrients for agricultural crops. However, studies have shown that E. coli O157:H7 can survive in manure for >3 months after defecation (1, 2, 21, 26). The ability of this bacterium to survive in animal manure is both an environmental and a food safety concern.
Efforts to decrease the shedding and persistence of E. coli O157:H7 in cattle manure are ongoing, but few viable interventions have been identified. The feeding of hay to feedlot cattle may decrease bacteria such as E. coli O157:H7 from being shed (3, 7), but a specific mechanism to explain a decrease has not been documented. Treatment of manure or animal waste during storage or prior to land application has the potential for decreasing manure-borne pathogens, thereby reducing the risk of water and crop contamination (18, 31, 37). However, concerns pertaining to the cost and environmental impact of treatments are important considerations prior to their implementation by producers. Therefore, a variety of both economical and effective manure treatments need to be developed and tested.
Plant carboxylic phenols have been shown to inhibit certain pathogens (9, 28, 33, 39), and in grasses used as cattle forages, their concentrations range from 2 to 10 g/kg (6, 19). These compounds are synthesized from phenylalanine via a cinnamic acid intermediate to phenylpropanoid compounds (19), and the predominant phenylpropanoid compounds in many forages are para-coumaric acid and ferulic acid (12, 25, 30). The phenolic acids are often conjugated to sugars in plants and may play a role in protecting plants from pathogens (12, 30). However, the antimicrobial effects of these plant compounds against pathogens in the complex fecal or manure environment are unknown. The objectives of this study were to evaluate the survival of E. coli O157:H7 in feces from cattle fed different types of diets and to determine if amendments with trans-cinnamic, coumaric, or ferulic acid affected the survival of this pathogen in cattle feces. Information garnered from this study will identify candidate plant compounds with antimicrobial activity in the fecal environment that may be useful as dietary additives or manure treatments.
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200 g/animal) were compiled for each diet and mixed well for laboratory study.
In subsequent studies to determine the potential for forage phenolic acids to decrease the viability of E. coli O157:H7 in bovine feces, fresh feces were collected from cattle feedlot pens located at MARC. The pens have packed dirt floors with concrete aprons extending from the feed trough, where most fecal samples were collected. The beef steers (approximately 250 to 450 kg, or 9 to 10 months of age) were being fed either corn silage (MARC feedlot growing diet; 87.5% corn silage and 12.5% cracked corn [base diet]) or cracked corn (MARC feedlot finishing diet; 69% cracked corn and 31% corn silage [base diet]). The corn silage and cracked-corn base diets were supplemented, as fed, with a 2.5% or 4.5% complete liquid supplement to provide additional dietary nitrogen (as urea), vitamin A, vitamin E, calcium, phosphorus, and salt. Feces were collected on four occasions over an 8-week period (June to August) from representative pens. A minimum of eight undisturbed fecal samples (
2 kg of feces total) were collected, with little soil contamination, and were compiled for each experiment.
Bacterial cultures.
Escherichia coli O157:H7 Strr strains 43985 and MARC S-1 were maintained throughout the experimental periods on tryptic soy agar plates supplemented with 250 µg/ml streptomycin. Prior to inoculation, colonies were picked and grown overnight at 37°C in tryptic soy broth supplemented with 250 µg/ml streptomycin. The cultures were then removed from the incubator and allowed to sit at room temperature for at least 24 h to acclimate to laboratory temperatures.
Fecal inoculations and incubations.
The fecal samples were analyzed prior to inoculation with the laboratory strains and did not contain indigenous Strr bacteria at the lowest dilution. To determine the survival of E. coli O157:H7 in feces from cattle fed the growing diets, laboratory-acclimated cultures of E. coli O157:H7 Strr strains 43985 and MARC S-1 were diluted in buffered peptone water to yield approximately 108 cells for each culture in a 2-ml cocktail, as determined by plate counts. In preliminary trials with cattle feces, a 2-ml inoculation cocktail volume per 100 g of feces consistently yielded 5.9 ± 0.1 log10 streptomycin-resistant cells per g feces after being mixed in sterile Whirl-Pak bags (NASCO, Fort Atkinson, WI) by hand massage for at least 5 minutes, and this protocol was followed in all subsequent experiments. The inoculated feces were placed into deep cell culture dishes (100 x 25 mm) and maintained upright and loosely covered in the laboratory at room temperature throughout the experiment. Incubations for each diet treatment were performed in duplicate.
To determine if phenolic acid compounds common to forage plants have an antimicrobial capacity, fecal composites were collected from pens housing animals consuming either a corn silage or cracked-corn diet, inoculated (as described above) with E. coli O157:H7 strains, and treated with phenolic acid compounds common to forages. Trans-cinnamic, para-coumaric, and ferulic acids were added individually as dry compounds to 200 g of inoculated feces at 0.1 or 0.5% of the wet fecal weight in separate plastic bags. Each bag with amended inoculated feces was mixed well by hand massage for 10 min. The fecal samples were then placed into deep culture dishes and maintained loosely covered in the laboratory at room temperature throughout the experiment. Fecal samples were collected on four occasions for either the corn silage or corn diets, and incubations for each treatment were performed in duplicate.
Viable cell counts.
Viable counts were determined by counting the CFU of streptomycin-resistant bacterial cells plated onto MacConkey sorbitol agar containing 250 µg/ml streptomycin. The CFU were determined at time zero with freshly inoculated feces and at the same relative time each assay day thereafter by serial dilution of a 1-g fecal sample. Aliquots (100 µl) of the appropriate dilutions were spread onto individual plates. Colonies were counted after the plates were incubated overnight at 37°C. Colonies were visually typical of E. coli O157:H7 and were confirmed to be E. coli O157 by agglutination using anti-O157 antibodies (Escherichia coli O157 test kit; Oxoid Ltd., Hampshire, England) if questionable. The inoculated feces were assayed until no cells were recovered from the lowest dilution (101) for at least two consecutive assays. In cases where rapid death was observed, no viable cells were found for up to 14 days after death. The viable counts were transformed to log10 equivalents for analysis. The detection limit was 1.5 log10 CFU per g feces.
Chemicals and analyses.
Chemicals and antimicrobials were purchased from Sigma-Aldrich Chemicals (St. Louis, MO). Bacterial growth media and buffers were Difco brand (Becton-Dickinson Company, Sparks, MD). The fecal pH was determined with 0.5 g of freshly composited feces suspended in 2.5 ml of distilled water.
Statistics.
All incubations were performed in duplicate for each fecal collection or treatment, and the coefficients of variation for duplicate pairs were <10%. Means and standard errors of the means are reported for all treatment effects. The statistical significance of treatment means were determined using Student's t test, and linear regressions were fit using least-square means by KaleidaGraph for the Macintosh, version 3.5x (Synergy Software, Reading, PA).
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FIG. 1. Effect of diet and time on diet on the viability of E. coli O157:H7 in inoculated feces. Fecal samples were collected from animals consuming either bromegrass hay () or corn silage ( ) for 4 weeks (a) or 8 weeks (b). The dotted line denotes the limit of detection for viable counts. Slopes (not shown in figure) were fit to the decreases in viable counts and represent the death rates (log10 CFU/g feces/day) of the inoculated strains.
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The time-dependent decreases in viable cells were nearly linear when expressed in log10 form (R2 > 0.7). The slopes of the lines represent death rates for E. coli O157:H7 (log10 CFU/g feces/day) and are shown in Fig. 2. The death rate was 0.12 log10 CFU/g feces/day in feces from animals consuming bromegrass hay for only 4 weeks. In fecal samples from animals consuming bromegrass hay for 8, 12, and 16 weeks, the E. coli O157:H7 death rates were not significantly different from each other (average rate, 0.036 log10 CFU/g feces/day; P > 0.5) but were significantly lower (P < 0.01) than the E. coli O157:H7 death rate in feces collected on week 4. The E. coli O157:H7 death rates in feces from animals consuming corn silage were not significantly affected by the time on the diet (4, 8, 12, or 16 weeks), and the average death rate was 0.074 log10 CFU/g feces/day, a value significantly different from the observed rates for bromegrass hay feces (P < 0.05).
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FIG. 2. Death rates (log10 CFU/g feces/day) of E. coli O157:H7 cells inoculated into feces from animals consuming bromegrass hay for 4 weeks (first column), bromegrass hay for 8, 12, and 16 weeks (second column), or corn silage for 4, 8, 12, and 16 weeks (third column). All data presented are averages with respective standard errors, and the averages are significantly different from each other (P < 0.05).
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FIG. 3. Recovery of E. coli O157:H7 over time from inoculated feces following no treatment or treatment with 0.5% trans-cinnamic acid or 0.5% para-coumaric acid. Fecal samples were collected from animals consuming a corn silage diet. Slopes (not shown in figure) were fit to the decreases in viable counts and represent the death rates (log10 CFU/g feces/day) of the inoculated strains.
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FIG. 4. Effects of added trans-cinnamic, para-coumaric, and ferulic acids on the death rate of E. coli O157:H7 in feces from animals fed corn silage. All data presented are averages with respective standard errors from four experiments.
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FIG. 5. Recovery of E. coli O157:H7 over time from inoculated feces following no treatment or treatment with 0.5% trans-cinnamic acid or 0.5% para-coumaric acid. Fecal samples were collected from animals consuming a cracked-corn diet. Slopes (not shown in figure) were fit to the decreases in viable counts and represent the death rates (log10 CFU/g feces/day) of the inoculated strains.
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FIG. 6. Effects of added trans-cinnamic, para-coumaric, and ferulic acids on the death rate of E. coli O157:H7 in feces from animals fed cracked corn. All data presented are averages with respective standard errors from four experiments.
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FIG. 7. Effect of initial fecal pH on viability of E. coli O157:H7 in untreated bovine feces ( ) and in bovine feces treated with 0.5% trans-cinnamic acid (). Feces were collected from animals consuming either corn silage (pH 5.9 to 6.3) or cracked corn (pH 5.3 to 5.8).
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The feeding of hay (timothy-grass hay) was proposed early as a dietary intervention to possibly control E. coli O157:H7 shedding (7). Reductions in acid-resistant E. coli levels in feces were noted when animals were fed hay for <2 weeks, but no specific mechanism to explain these effects has been reported (3). Other reports did not observe a benefit in feeding hays (timothy-grass or alfalfa-legume) over longer periods to sheep (21, 22) or cattle (15, 36), and in these experiments, E. coli O157:H7 was persistently shed in the feces of pathogen-dosed animals fed hay. Based on our results with bromegrass hay in relation to published observations, any observed anti-E. coli O157:H7 benefits of hay feeding may disappear as the ruminant animal fully adapts to the hay diet, which may explain these discrepancies.
Plants have bound phenolic acids that are released to help control bacterial pathogen invasion (8, 12, 30), and in vitro studies have shown that plant phenolic acids can rapidly kill many human-pathogenic bacteria (13, 20, 28, 39). In forages, phenolic acids are derived from cinnamic acid and are often conjugated to carbohydrates or carbohydrate structures (12, 25, 30). These compounds, commonly known as hydroxycinnamic acids, include para-coumaric, ferulic, synapic, and caffeic acids. The phenolic acid content can vary in individual amounts among plant species, but the total extractable phenolics may be >1% of the plant dry matter (6, 19). The effect of these compounds in the gastrointestinal system may not be fully appreciated.
In ruminants that are fully adapted to forage diets, plant phenolic acids are metabolized in the rumen (6, 25). However, information about phenolic acid metabolism in the rumens of animals fed grain is lacking. A previous report (22) suggested that E. coli O157:H7 was shed less in feces from animals with corn diets than in those from animals with hay diets, but the animals fed corn were also fed alfalfa, and it should be noted that the fiber content of the feces of these animals was actually higher than that for animals fed hay. Animals on grain diets have little capacity to digest fiber in the rumen (34), and as a consequence, when they are fed hay, more fiber with phenolic acids passes into the lower gastrointestinal system, where liberated phenolic acids would have the greatest effect on E. coli O157:H7 populations.
Typically in feedlots in the United States, beef cattle are fed high-energy diets based on corn, and E. coli O157:H7 can persist in the manures. To determine if forage phenolic acids could affect the viability of E. coli O157:H7 in feces from animals fed corn silage or cracked corn, we added trans-cinnamic, para-coumaric, or ferulic acid to cattle feces inoculated with E. coli O157:H7. The phenolic acid treatments decreased the viable cell counts of E. coli O157:H7 in feces from corn silage or cracked-corn diets in a dose-dependent response. However, the most prominent effect was in the feces from animals fed cracked corn, and the effectiveness differed between the phenolic acids.
Cinnamic acid was the most effective compound tested in feces, and its effectiveness was related to the fecal pH (Fig. 7); a similar response of trans-cinnamic acid to pH was observed previously against Listeria monocytogenes in pure culture (39). A higher dose (0.5%) of para-coumaric acid reduced the number of E. coli O157:H7 cells in feces from the corn silage and cracked-corn diets similarly, but the lower dose (0.1%) was only effective in feces from animals fed cracked corn. Ferulic acid (0.5%) was more effective in feces from animals fed cracked corn, which is similar to the response obtained with 0.1% para-coumaric acid. These dietary differences may be related to higher ferulic and coumaric acid contents in corn silage than in corn grain (12) and to selection for gastrointestinal microorganisms capable of partially degrading these phenolic acids in the feces. Nevertheless, these compounds still had significant antimicrobial capabilities in the feces.
Escherichia coli O157:H7 is generally recognized as a problem in feces from concentrated animal operations where animals are fed low-forage/high-energy diets. In our work, the death of E. coli O157:H7 was fastest in the feces of animals fed a high-corn diet (Fig. 4 and Fig. 6), and this effect seemed to be associated with a lower fecal pH (Fig. 7). Nonetheless, viable counts were recovered from the feces of animals on the diets for appreciably long periods of time (>20 days), and this would be a problem for manure management. Considering that E. coli O157:H7 can persist as a contaminant in soil and on crops for months after manure application or irrigation (16, 17, 27), the reduction or elimination of E. coli O157:H7 in production animal systems would be ideal.
To our knowledge, the plant phenolic acids have not been associated with decreased pathogen survival in feces. In our initial study with bovine diets and the viability of E. coli O157:H7 in the feces, we did not anticipate that the viability would be affected by the time on the diet, and as a consequence, we did not sample these feces for phenolic acids. Recognizing the differences with the time on the diet, the adaptation of ruminants to forages, and the ability of plant phenolic acids to affect pathogens in in vitro studies (13, 20, 28, 39) led us to analyze the effects of phenolic acids in bovine feces. The fact that we observed significant effects with concentrations as low as 0.1% of the phenolic acids, an amount less than that found in many forages, suggests a potential role for controlling pathogens in the gastrointestinal system.
The treatment of stored animal manures with plant essential oils has decreased the amounts of pathogens (37), and our work suggests that phenolic acids may also be useful for similar treatments. In addition, extrapolation of our work with bovine feces to the gastrointestinal system suggests that supplementation of plant phenolic acids to the diets of feedlot animals may be an exploitable intervention. However, more research needs to be done to determine the feasibility of this approach. Recent works by Duncan et al. (9, 10) have demonstrated the potential of dietary esculin and esculitin, which are plant coumarin compounds, to decrease viable E. coli O157:H7 in rumen fluid and colonic contents. The study of plant phenolic acid metabolism in ruminants has been limited to forage-adapted animals (6, 25), and limited information is available about their metabolism in animals fed feedlot diets. Future studies will need to determine the stability of phenolic acids in animals fed grain and then determine their dietary potential to reduce pathogen shedding from feedlot cattle.
Mention of trade names or commercial products in this publication is solely for the purpose of providing specific information and does not imply recommendation or endorsement by the U.S. Department of Agriculture.
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