Source: VIRGINIA POLYTECHNIC INSTITUTE submitted to
DETERMINING THE SURVIVAL CHARACTERISTICS OF SELECTED FOODBORNE PATHOGEN STRAINS IN MANURE-AMENDED AGRICULTURAL SOILS
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
NEW
Funding Source
Reporting Frequency
Annual
Accession No.
1014801
Grant No.
(N/A)
Project No.
VA-160074
Proposal No.
(N/A)
Multistate No.
(N/A)
Program Code
(N/A)
Project Start Date
Jan 1, 2018
Project End Date
Dec 31, 2022
Grant Year
(N/A)
Project Director
Strawn, LA, K..
Recipient Organization
VIRGINIA POLYTECHNIC INSTITUTE
(N/A)
BLACKSBURG,VA 24061
Performing Department
Food Science & Technology
Non Technical Summary
In the United States (US), contaminated produce is estimated to cause over 1.1 million illnesses, 7,125 hospitalizations, and 134 deaths annually, with associated costs of $1.4 billion. Should a producer be involved in litigation following an outbreak where negligence is directly pushed back onto the grower, costs are estimated to exceed $100,000 per case of foodborne illness (35, 36). Negative media and press from such an outbreak could render produce from Virginia non­ marketable and threaten the sustainability of a 100+ million-dollar industry (38). A recent US agricultural census in 2015, ranked Virginia 9th in direct vegetable sales, producing 217,343,742 on 3,415 farms (38). In addition to their substantial economic impact, foodborne illnesses also have an impact on human well-being in the US. When ranking the top 10 pathogen-food combinations in terms of annual disease burden, "Salmonellaproduce" ties for 8th; quality­ adjusted life year loss (2,781), cost of illness ($548,000,000); number of illnesses (170,264), hospitalizations (3,204), and deaths (1). Since 2002, produce grown in the Delmarva region (Delaware, Maryland Eastern Shore and Virginia Eastern Shore) have been linked to six foodborne disease outbreaks caused by Salmonella Newport. Specifically, produce contaminated with Salmonella Newport reportedly caused illness in 333, 72, 115, 65, 51 and 275 persons in 2002, 2005, 2006, 2007, 2010, and 2014 (21). This data highlights the impact of foodborne pathogen contamination on produce and the resulting impact to public health. Therefore, applied research is needed to assist the produce industry (e.g., growers, suppliers, etc.) in developing science-based recommendations to mitigate potential foodborne pathogen contamination events, and reduce the likelihood of foodborne outbreaks. Currently, the safety of produce is based on the implementation of Good Agricultural Practices (GAPs) to prevent microbial contamination during growing, harvesting, and postharvest handling. The goal of a GAPs program is to provide stakeholders with science-based recommendations on where microbial contamination may originate, survive, and transfer to fresh produce. A successfully implemented GAPs program should minimize the likelihood of contamination events and subsequent foodborne illnesses. While the research community and produce industry have gained a better understanding of how produce items may become contaminated (through water, soil amendments, sick workers), knowledge gaps remain including the risk of specific soil amendments or the rates specific pathogens need to die over time). Furthermore, the Food Safety Modernization Act's Produce Safety Rule has yet to set standards on raw manure application to produce fields until more research can be performed (defered action).Therefore,the purpose of this project is to determine the survival characteristics of selected foodborne pathogen strains, specifically Salmonella spp. (12 strains), Escherichia coli (E. coli) O157 (8 strains), and non-O157 Shiga toxin-producing E. coli (STEC) (7 strains) in raw manure-amended agricultural soils. We will use raw poultry manure to study the survival of Salmonella and we will use raw cattle manure for the study of E. coli O157 and non-O157 STEC. The raw biological soil amendment and pathogen pair was selected as prior studies, have shown those biological soil amendments may contain the respected pathogen. Additionally, the project will evaluate the survival of these pathogens in two different soil types commonly found in agricultural environments (sandy-loam andclay-loam soils). The data will also be used to develop models for use of raw manure in agricultural settings and provide recommendations (to growers, produce industry) for their application to fields where produce will be grown.
Animal Health Component
0%
Research Effort Categories
Basic
25%
Applied
75%
Developmental
0%
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
72240101100100%
Knowledge Area
722 - Zoonotic Diseases and Parasites Affecting Humans;

Subject Of Investigation
4010 - Bacteria;

Field Of Science
1100 - Bacteriology;
Goals / Objectives
Produce continues to be linked to foodborne outbreaks since many fruits and vegetables are consumed raw without a processing step that could inactivate microorganisms (2). Over a 15-year period beginning in 1990, produce was linked to 713 outbreaks and 34,049 cases of foodborne illnesses (3). Most recently in the US, outbreaks related to Escherichia coli O157:H7, O145, O26, Salmonella serovars, and Listeria monocytogenes have been linked to tomatoes, peppers, cantaloupe, mangoes, cucumbers, spinach, lettuce, and sprouts (4-19).The Food Safety Modernization Act (FSMA; which incorporates seven different food safety rules) was passed by Congress and signed into law by president Obama in 2011. FSMA emphasizes a preventive approach to food safety rather than responding and reacting to outbreaks (or contamination events). One of the seven rules in FSMA, the Produce Safety Rule (PSR), regulates the standards for the growing, harvesting, packing and holding of produce for human consumption (20). As of November 27, 2015, the final Produce Safety Rule was published in the federal registrar and provides standards for agricultural water, biological soil amendments, sprouts, worker health and hygiene, domestic and wild animals, equipment, building and tools, and other areas. In the final rule, the Food and Drug Administration (FDA) deferred action on the appropriate time interval or intervals between the application of untreated biological soil amendments of animal origin (including raw manure) and crop harvesting. While GAPs are voluntary, FSMA PSR compliance will be mandatory for many (as outlined by their size and profits, 20). Thus, the purpose of this project is to determine the survival characteristics of selected foodborne pathogen strains, specifically Salmonella spp. (12 strains), Escherichia coli (E. coli) O157 (8 strains), and non-O157 Shiga toxin-producing E. coli (STEC) (7 strains) in raw manure-amended agricultural soils. We will use raw poultry manure to study the survival of Salmonella and we will use raw cattle manure for the study of E. coli O157 and non-O157 STEC. The raw biological soil amendment and pathogen pair was selected, as prior studies have shown those biological soil amendments may contain the respected pathogen (25, 26). Additionally, the project will evaluate the survival of these pathogens in two different soil types commonly found on the Delmarva Peninsula (sandy-loam) and mainland Virginia (clay-loam) (37). The data will also be used to develop models for use of raw manure in agricultural settings and provide recommendations (to growers, produce industry) for their application to fields where produce will be grown. Specific objectives include:Salmonella survival "strain variability" (12 strains) in two types of soil (sandy and clay) with simulated soil moistureE. coli O157 survival "strain variability" (8 strains) in two types of soil (sandy and clay) with simulated soil moistureNon-O157 STEC survival "strain variability" (7 strains) in two types of soil (sandy and clay) with simulated soil moistureDevelopment of models to provide guidance on factors that influence the likelihood of pathogen survival in manure-amended soils
Project Methods
Research will be conducted at the Eastern Shore Agriculture Research and Extension Center in Painter, VA. The Biosafety Level, BSL-2 Greenhouse will be used for individual experiments. The approach for addressing each objective is described in greater detail below. Objectives 1-3. Investigate Salmonella (Y1), E. coli O157 (Y2) and non-O157 STEC (Y3) survival "strain variability" in two types of soil with simulated soil moisture.This set of experiments will be conducted at the Virginia Tech Eastern Shore AREC "Biosafety Level 2" Greenhouse. Whenever appropriate, standard methods such as those from the Compendium of Methods for the Microbiological Examination of Foods, the U.S. Food and Drug Administration's Bacteriological Analytical Manual (BAM), or other applicable sources (27-31), will be used for the enumeration or identification of organisms.Experiments will be arranged in a randomized complete block design with three replications for a total of 72 planting pots (3 replicates × 12 strains × 2 soil types) for Salmonella, 48 planting pots (3 replicates × 8 strains × 2 soil types) for E. coli O157:H7 and 42 planting pots (3 replicates × 7 strains × 2 soil types) for non-O157 STEC. The experiments for all strains of a target organism will be performed simultaneously, with each replication occurring at different times. For each replication, positive (Green-Fluorescent Protein-tagged pathogen strain) and negative (no pathogen) control pots will also be included. See timeline for further details. Methods are detailed for the "strain variability" experiments. The methodology framework is similar, with minor details due to organism differences (e.g., Salmonella vs. E. coli O157:H7 selective media agars).Manure. Fresh poultry or cow manure will be obtained from local chicken or cow operations in Virginia. Key descriptive physical/chemical properties of manure samples will be collected including pH, moisture content, ammonia-N, nitrogen, and phosphorus. In order to mimic the real production environment, manure will not be autoclaved to kill resident microorganisms, but, if possible, the microflora will be characterized.Soil. Sandy-loam or clay-loam soil will be obtained from the 0-20 cm layer of agricultural farms located in Painter and Petersburg, Virginia, respectively. Soil will be collected prior to each replication. Soil samples will be tested for key descriptive physical/chemical properties including pH, moisture content, ammonia-N, nitrogen, nitrate, and carbon. Soil will be weighed into 2,000-g portions in new plastic pots and sterilized distilled water will be added to bring the soil moisture to levels typically observed in agricultural fields (approximately 12-15% sandy-loam and 22-25% clay-loam). Bacteria. We will select up to 12 Salmonella, 8 E. coli O157:H7 and 7 non-O157 STEC strains for use in experiments. Strains considered will include:Strains used in previous studies by USDA-ARS and FDA (21, 24)Strains that have been associated with outbreaks from produce commodities of interest (4-19, 22)Other significant strains (e.g., environmental strains), when outbreak strains are unavailable (23).Strains isolated by Virginia Tech Eastern Shore in previous studies (unpublished Strawn, unpublished Gu)Inoculation. Frozen stock cultures of bacterial strains are typically stored in glycerol stock solutions at -80°C. Prior to use, strains are streaked onto non-selective media supplemented with selective agents as appropriate. Inocula will be prepared from media or broth cultures and will be washed prior to use. Careful consideration will be taken to ensure inocula will be prepared similarly to the physiological state of the organism in manure and produce growing environment, by using appropriate growth media and adaptation procedures. Each inocula will be prepared at a level of approximately 7-8 log CFU/mL (24). Inocula will then be incorporated into the amended soil mixture and placed in pots. Briefly, soil will be amended with poultry litter or raw manure at a commercial agricultural standard rate of 4 kg/acre (M. Reiter, personal communication). This mixture (soil amended with poulty litter or raw cow manure) and inocula will be transferred to a sterile plastic bag, where it will be thoroughly homogenized (combined using a 30-s shake, 30-s rub, 30-s shake, repeat method). In total, 2000-g of inoculated manure-amended soil will be transferred to separate pots (one pot for each strain and soil type). The target inoculum in the amended soil (in each pot) will be approximately 4-5 log CFU/g. Test trial experiments will be performed prior to the study to determine the starting inoculum level that will yield a 4-5 log CFU/g in amended soil mixture. Throughout the incubation, the moisture content of the samples will be maintained by weekly weighing and addition of sterilized distilled water, as needed. Soil moisture levels will be targeted according to traditional precipitation data. Manure, soil, and manure-amended soil samples without inoculation will serve as controls.Sampling and enumeration. Organism counts will be determined at 0, 0.167, 1, 2, 4, 7, 14, 21, 28, 56, 84, 112, 168, 210, 252, and 336 days post-inoculation. If possible, more sampling points within the first 24 h will be added (e.g. 8 h time point), if necessary after test trials. Sampling and enumeration will be performed according to standard methods for Salmonella and STEC protocols by the Compendium of Methods for the Microbiological Examination of Foods and the U.S. Food and Drug Administration's Bacteriological Analytical Manual (27-31).Environmental Measurements. Select conditions within the greenhouse will be monitored during all trials. Air temperature and relative humidity will be monitored with measurements being recorded every 1 h. Soil samples (100 g) will be taken from control pots (no pathogens) and sent to the Waypoint Soil Testing Laboratory in Richmond, Virginia where they will determine soil pH, carbon content, amount and form of nitrogen present, among other soil variables.Objective 4. Development of models to provide guidance on factors that influence the likelihood of pathogen survival in manure-amended soil with different moisture conditions (Y4-5). In the first three years of this research a large amount of survival data will be collected and managed in excel spreadsheets. Each pathogen strain survival data (including pathogen enumeration, weather, soil data sets, etc.) will be used to support the development of risk models to determine the likelihood of produce contamination in fields with raw manure-amended soils. Once models have been developed, key recommendations will be derived for the produce industry.Data analysis. Statistics will be performed in appropriate software, such as SAS (SAS release 9.4, SAS Institute Inc., Cary, North Carolina). The survival of the strains will be compared by each soil type and over time for each replication, as well as overall (all three replications). Population data for each strain will be analyzed and fit into models to assess survival trends; for example, the analysis of variance with repeated measures across sampling times will be performed to determine whether general differences exist between the different strains (ANOVA using the PROC GLIMMIX procedure). Treatments (e.g., soil type or strain) will be treated as fixed factors, whereas location and replication will be treated as random. Means will be separated using Fisher's protected LSD at P=0.05 when appropriate.

Progress 10/01/19 to 09/30/20

Outputs
Target Audience:Growers of fresh produce and other produce stakeholders (e.g., buyers), regulatory personnel, food and environmental scientists, other scientists and researchers. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?Training in good laboratory practices and technical skills associated with the microbiological practices wereprovided to technical staff; as well as statistical modeling was communicated to students and other professionals. How have the results been disseminated to communities of interest?Project goals and data have been communicated at food safety meetings to regulatory personnel, produce stakeholders, and other scientists. Additionally, a publication is under review on Salmonella modeling results. What do you plan to do during the next reporting period to accomplish the goals?Subsequent modelingwill be performed on E. coli data. A draft publication for E. coli data will be prepared and hopefully submitted by end of the reporting period.

Impacts
What was accomplished under these goals? The use of untreated biological soil amendments of animal origin (BSAAO) has been identified as one potential mechanism for the dissemination and persistence ofpathogensin the produce growing environment. Data on factors influencingpathogensconcentration in amended soils are therefore needed. All experiments have been performed for Salmonella, E. coli O157, and non-O157 STEC survival in sandy- and clay-loam soils. All descriptive statistics have been completed, as well as all Salmonella models. Models are in progress for E. coli O157 and non-O157 STEC. Salmonella models were developed to (i) compare die-off between 12 Salmonella strains following inoculation in amended soil, and (ii) characterize any significant effects associated with soil-type, irrigation regime, and amendment on Salmonella survival and die-off. Three greenhouse trials were performed using a randomized complete block design. Each strain (~4 log CFU/g) was homogenized with amended or non-amended sandy- or clay-loam soil. Salmonella levels were enumerated in 25g samples 0, 0.167 (4h), 1, 2, 4, 7, 10, 14, 21, 28, 56, 84, 112, 168, 210, 252, and 336 d post-inoculation, or until two consecutive samples were enrichment negative. Regression analysis was performed between strain, soil-type, irrigation, and (i) time to last detect (survival) and (ii) concentration at each time-point (die-off rate). Similar effects of strain, irrigation, soil-type, and amendment were determined using the survival and die-off models. Strain explained up to 18% of the variance in survival, and up to 19% of variance in die-off rate. On average Salmonella survived for 129 d in amended soils, however,Salmonella survived, on average, 30 days longer in sandy-loam soils than clay-loam soils [95% Confidence Interval (CI)=-45, -15; P<0.001), with survival time ranging from 84 to 210 days for the individual strains during daily irrigation. Salmonella also survived, on average,128 d longer when irrigated weekly, compared to daily (CI=101, 154; P<0.001), and 89 d longer in amended soils, than non-amended soils (CI=61, 116; P<0.001). Interestingly, when strain-specific associations were investigated using regression trees, we found that although most strains survived longer in clay-loam soil, S. Javiana and S. Saintpaul survived longer in sandy-loam soil. Overall, this study provides insight into Salmonella survival following contamination of field soils by BSAAO. Specifically, Salmonella survival may be strain-specific as affected by both soil characteristics and management practices. These data can assist in risk assessment and strain selection for use in challenge and validation studies.

Publications

  • Type: Journal Articles Status: Under Review Year Published: 2020 Citation: C. Bardsley, D. Weller, S. Rideout, D. Ingram, Y. Chen, D. Oryang., and L.K. Strawn. Strain, Soil Type and Irrigation Regime Influence Salmonella Survival in Poultry Litter Amended Sandy and Clay Soils". Frontiers in Microbiology. Under Review


Progress 10/01/18 to 09/30/19

Outputs
Target Audience: Growers of fresh produce and other produce stakeholders (e.g., buyers), regulatory personnel, food and environmental scientists, other scientists and researchers. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided? Training in good laboratory practices and technical skills associated with the microbiological practices was provided to technical staff. How have the results been disseminated to communities of interest? Project goals and data have been presented at a food safety annual conference (2019) to regulatory personnel,produce stakeholders, and other scientists. Additionally, a publication was accepted in Frontiers Microbiology, as well as a peer-reviewed extension publication on soil amendments. What do you plan to do during the next reporting period to accomplish the goals? Subsequentanalyses will be performed on E. coli datasubmitted. A publication will be submitted for Salmonella data. Work on Objective 4 and begin modeling analyses.

Impacts
What was accomplished under these goals? The research experiments associated with Objective 2/3were completed: E. coli survival "strain variability" (15strains) in two types of soil (sandy (SL) and clay (CL)) with simulated soil moisture. Greenhouse experiments were arranged in a randomized complete block design totaling 108pots (3 replicates × (15strains (daily water) +3 strains (weekly water) × 2 soil types). Strains were adapted to 80 μg/mL rifampcin(RIF). Each culture was mixed with each soil type and bovine manure (BM). The target inoculum was 4-5 log CFU/g. All strains were exposed to daily water application to maintain soil moisture, while three of the strains were exposed to weekly water application. Soil was sampled at 0, 0.167, 1, 2, 4, 7, 14, 21, 28, 56, 84, 112, 168, 210, 252, and 336 days post-inoculation. Population levels were enumerated on RIFselective agar. An MPN method was used to detect lower levels (-0.6 log MPN/g). Significant differences were analyzed using Tukey's HSD test P<0.05.Loggers indicated soil moisture targets were maintained within +/-2%. The greenhouse temperature and relative humidity ranges were 21 to 29C (average 25C) and 51-71% (average 61%), respectively. All negative control pots were negative. Overall, BM supported growth and increased survival ofE. coliin SL and CL soils. E. colitype (generic vs. pathogenic), and irrigation regime impacted the survival ofE. coliin BM amended soils.GenericE. colistrains survived longer than pathogenic strains in SL and CL soils amended with BM.There does not appear to be any significant differences inE. colistrain survival in SL and CL soils amended with BM.E. colistrains (subjected to daily irrigation) survived in SL and CL soils amended with BM for 168-252 d. Strain B (TVS cocktail) had the longest survival at 336 d.E. colistrains (subjected to weekly irrigation) survived in SL and CL soils amended with BM for 210-336 d. Strain B (TVS cocktail) had the longest survival at 336 d.E. colistrain B (TVS cocktail) survived approximately twice as long in SL and CL soils amended with BM (252 d), compared to SL and CL soils without BM (112 d).Only a few strains exhibitedE. coligrowth during the experiments, and if growth occurred it was within the first week.

Publications

  • Type: Journal Articles Status: Accepted Year Published: 2019 Citation: Gu, G., L.K. Strawn, J. Zheng, E.A. Reed, S.L. Rideout. 2019. Diversity and dynamics of Salmonella enterica in water sources, poultry litters, and field soils amended with poultry litter in a major agricultural area of Virginia. Frontiers in Microbiology.
  • Type: Conference Papers and Presentations Status: Accepted Year Published: 2019 Citation: Strawn, L.K.*, C. Bardsley, S. Rideout, D. Ingram, Y. Chen, J. Van Doren, D. Oryang. Strain, Soil Type and Irrigation Regime Influence Salmonella Survival in Poultry Litter Amended Sandy and Clay Soils  P2-231. 2019 International Association of Food Protection Annual Meeting, Louisville, KY, July 23, 2019.


Progress 01/01/18 to 09/30/18

Outputs
Target Audience: Growers of fresh produce and other produce stakeholders (e.g., buyers), regulatory personnel,food and environmental scientists, other scientists and researchers. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided? Training in good laboratory practices and technical skills associated with the microbiological practices was provided to technical staff. How have the results been disseminated to communities of interest?Project goals and preliminary datahave been presented at a research symposium (2018) to regulatory personnel and some produce stakeholders. Y1data and subsequent analyses will be submitted for an IAFP abstract this year (2019) for dissemination to a wider audience. What do you plan to do during the next reporting period to accomplish the goals?Y1data and subsequent analyses will be submitted for an IAFP abstract this year (2019) for dissemination to a wider audience. Objective 2 of the study will be performed:E. coliO157 survival "strain variability" (8 strains) in two types of soil (sandy and clay) with simulated soil moisture. As well as data analyses on Objective 1 and presentation ofObjective 1 findings at a conference (goal is IAFP Annual Meeting 2019).

Impacts
What was accomplished under these goals? The research experiments associated with Objective 1 were completed:Salmonellasurvival "strain variability" (12 strains) in two types of soil (sandy (SL) and clay (CL)) with simulated soil moisture.Greenhouse experiments were arranged in a randomized complete block design totaling 90 pots(3 replicates × (12 strains (daily water) +3 strains (weekly water) × 2 soil types). Strains were adapted to 50μg/mL nalidixic acid (NA). Each culture was mixed with each soil type and PL. The target inoculum was 4-5log CFU/g. All strains were exposed to daily water application to maintain soil moisture, while three of thestrains were exposed to weekly water application. Soil was sampled at 0, 0.167, 1, 2, 4, 7, 14, 21,28, 56, 84, 112, 168, 210, 252, and 336days post-inoculation.Population levels were enumerated on NA selective agar. An MPNmethod was used to detect lower levels (-0.6log MPN/g). Significant differences were analyzed usingTukey's HSD test P<0.05. Loggers indicated soil moisture targets were maintained within +/-2%. The greenhouse temperature and relative humidity ranges were 21 to 29C (average 25C) and 51-71% (average 61%), respectively. All negative control pots were negative. Salmonella populations in non-PL amended SL and CL soils observed no significant growth, while Salmonella populations in PL amended SL and CL soils observed significant growth within 24 h (1 d). Salmonella populations in non-PL amended SL and CL soils had limited survival (only 56 d), compared to PL amended SL and CL soils (using Salmonella serovar Newport; 112 d). While Salmonella populations demonstrate similar growth and survival curves, there is variablity in the 12 Salmonella strains investigated. Additionally, Salmonella strains exhibited variability when compared by the different soil types (SL and CL). In the SL and CL soils amended with PL, an initial decrease in Salmonella populations was observed within the first 4 h, before growth of approximately 1-3 log CFU/g by 24 h (1 d). Salmonella populations begin to decline depending on strain by 4-10 d. Salmonella survival was increased in weekly soil moisture maintenanced pots. In SL soils amended with PL, a spike was observed in Salmonella populations between 7 and 10 d when water was added to pots. Soil moisture was adjusted weekly (this trend was captured in all three cases due to the 10 d sampling time-point). In CL soils amended with PL, Salmonella populations followed similar growth and survival behavior regardless of soil moisture being adjusted daily or weekly. CL soils retain water better than SL soils.Salmonella populations survived longer in CL soils amended with PL with daily soil moisture monitored. In SL soil amended with PL, mostSalmonella strains survived until d 112, except Muenchen (d 84), Saintpaul (d 168), and Javiana (d 210). In CL soil amended with PL, mostSalmonella strains survived until d 168, except Muenchen (d 84), Meleagridis (d 84), Javiana (d 112), Montevideo (d 210) and Braenderup (d 210).Salmonellapopulations survived longer in both SL and CL soils amended with PL with weekly soil moisture monitored. This finding may be due to potential activation of stress response systems, or other factors. Further data analyses are pending.

Publications

  • Type: Journal Articles Status: Published Year Published: 2018 Citation: Gu, G., L.K. Strawn, D.O. Oryang, J. Zheng, E.A. Reed, A.R. Ottesen, R.L. Bell, Y. Chen, S. Duret, D.T. Ingram, M.S. Reiter, R.C. Pfuntner, E.W. Brown, S.L. Rideout. 2018. Agricultural practices influence Salmonella contamination and survival in pre-harvest tomato production. Front. Microbiol. https://doi.org/10.3389/fmicb.2018.02451.
  • Type: Conference Papers and Presentations Status: Other Year Published: 2018 Citation: Strawn, L.K. 2018. Determining the Survival Characteristics of Selected Foodborne Pathogen Strains in Manure-Amended Agricultural Soils. FDA Research Symposium.