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ENVIRONMENT, WELL-BEING, AND BEHAVIOR |
* USDA-ARS, Animal Waste Management Research Unit, Bowling Green, KY 42104; and USDA-ARS, Waste Management and Forage Research Unit, Mississippi State, MS 39762
1 Corresponding author: nlovanh{at}ars.usda.gov
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ABSTRACT |
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 TOP ABSTRACT INTRODUCTIONMATERIALS AND METHODSRESULTS AND DISCUSSIONREFERENCES |
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Key Words: microbial diversity • denaturing gradient gel electrophoresis • poultry litter • principal component analysis
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INTRODUCTION |
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TOPABSTRACTINTRODUCTIONMATERIALS AND METHODSRESULTS AND DISCUSSIONREFERENCES |
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Poultry litter is a valuable fertilizer source for crop production. However, its value as a fertilizer is reduced over time due to the significant losses of nitrogen attributed to the volatilization of ammonia (Lauer et al., 1976; Pain et al., 1987; Hartung and Phillips, 1994). Ammonia emission and subsequent deposition can be a major source of pollution, causing nitrogen enrichment, acidification of soils and surface waters, and aerosol formation. In the poultry house, ammonia emissions can also adversely affect the health, performance, and welfare of animals and human operators (Donham et al., 1977; Donham and Gustafason, 1982; Donham, 1990).
In addition to its use as fertilizer, poultry litter has nutritional value as feeds for ruminants (Smith, 1974; Jeffrey et al., 1998). However, there are concerns regarding the safety of feeding poultry litter to cattle due to potential infection by pathogenic microorganisms that may be present in poultry litter. Many pathogenic strains such as Listeria monocytogenes, Salmonella, Campylobacter spp., Clostridia spp., and Bordetella spp. have been found in poultry litter samples (Martin et al., 1998; Lu et al., 2003b).
Microbial diversity in poultry litter plays an important role in shaping the quality of the poultry litter as a fertilizer and as a nutritional feedstock, and influences malodor production and potential health risks. It is, therefore, essential to understand how the structure of microbial populations within poultry litter is influenced by the physical environment of the poultry house. This knowledge, in turn, could aid in the development of management practices that would reduce populations responsible for toxic air emissions (especially ammonia emissions) and pathogen incidence. Even though many studies have been done to classify microbial composition in poultry litter (Lovett et al., 1971; Nodar et al., 1990; Martin et al., 1998; Lu et al., 2003b; Fries et al., 2005), these classifications were only carried out on different types of poultry litters (e.g., poultry manure with different bedding materials). Research on spatial shifts in microbial population structure within poultry litter associated with physico-chemical properties is scarce and incomplete.
The aim of this work is to examine the spatial shifts in the microbial community structure in poultry litter using denaturing gradient gel electrophoresis (DGGE) and to evaluate how those shifts are associated with physical parameters. Principal component analysis (PCA) was used to determine the important factors that correlated with shifts in the microbial community structure. Understanding the contributing factors affecting microbial community structure may provide a rational basis for improving the design and optimizing the remediation options for toxic air and pathogenic reduction, whether these involve microscale biological treatment such as enzyme inhibition or physicochemical treatment such as alum amendment.
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MATERIALS AND METHODS |
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TOPABSTRACTINTRODUCTIONMATERIALS AND METHODSRESULTS AND DISCUSSIONREFERENCES |
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illustrates the sampling locations, with 3 sites spaced at 5 m across the building and 12 locations (12 m between) along the length of the building to create a 36 sample grid. To consider areas of frequent bird activity, specifically near feeders and waterers, 8 supplementary samples were taken in a crisscross routine between the feeders/ waterers. The feeder/waterer samples are shown as circles in Figure 1. Two feed lines were approximately 3.7 m from the center of the house, having a nipple water line 0.75 m on either side for a total of 4 water lines. A pocket meter (Kestril 3000, Nielson Kellerman, Chester, PA) reported house air temperature and relative humidity at 1 m above the floor. At the laboratory, litter moisture was determined by drying for 48 h at 65°C. A litter to deionized water ratio of 1:5 was used to determine pH for the samples.
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DGGE Analysis of Chicken Litter Microbial Populations
Bacterial community 16S rDNA (2 µL) from the 1:50 dilution was amplified with the bacterial specific primer set 341F-GC/907R, using the previously described PCR protocols (Casamayor et al., 2000) in a PTC-200 DNA thermal cycler (MJ Research, Las Vegas, NV). The guanine-cytosine (GC) designation on the 341F primer represents a 40-bp GC rich region on the 5' end of the primer necessary to prevent complete denaturation of the DNA strands during electrophoresis. Sequences were amplified using Ready-To-Go-PCR Beads (Amersham Pharmacia, Piscataway, NJ), with 800 nM each primer. Denaturing gradient gel electrophoresis was used to separate and characterize 16S rDNA by using a gradient of denaturants [100% denaturant solution consisting of a combination of 40% (vol/vol) formamide and 7 M urea] in a polyacrylamide gel (37.5:1) to separate DNA fragments according to melting behavior (i.e., sequence, melting domains). GelBond PAG Film (Cambrex BioSciences, Rockland, MA) was used during pouring of the DGGE gels to allow for easier manipulation of the polyacrylamide gel after electrophoresis. Then, 5 µL of PCR product was electrophoresed through a 30 to 60% denaturing gradient according to Nubel et al. (1997) for 4 h at 200 V in a BioRad DCode universal mutation detection (BioRad Laboratories, Hercules, CA). The DGGE gels were stained with the BioRad Silver Stain kit according to the manufacturer’s specifications, and the images were captured using an Epson Perfection 4990 Photo Scanner (Epson, Long Beach, CA). The DGGE fingerprint analysis was performed using the Fingerprint II software program (BioRad Laboratories) using the basic and clustering modules. The gel images were imported into the software and analyzed according to manufacturer’s specifications, with unweighted pair group method with arithmetic mean (UPGMA) analyses being performed based upon the banding patterns present in each gel lane. The strength of the clusters obtained from the UPGMA analysis was based on cophenetic correlations, which are an estimate of the faithfulness of a grouping within a dendrogram, with a score of 100 indicating that a grouping is extremely well supported.
DNA Sequencing and Phylogenetic Analysis
Relevant DGGE bands were excised using a sterile scalpel and forceps and placed into 150 µL of 10 mM Tris buffer. 0.1 mm Zirconia/Silica beads (BioSpec Products Inc., Bartlesville, OK) were added to each tube, and the samples were placed in a Fast Prep FP120 (Q-BIOgene) for 1 min at a speed of 5.5 m/s followed by overnight incubation at 4°C. Then, 2 µL of the solution was PCR amplified using the primer set (substituting an identical forward primer without the 40-bp GC clamp), reaction mixture, and thermocycling conditions discussed above. The resultant PCR product was cloned into the pCR2.1-TOPO plasmid using a TA TOPO Cloning Kit (Invitrogen) according to manufacturer’s specifications and sent to USDA-ARS MSA Genomics Laboratory (Stoneville, MS) for sequencing. The DGGE Band sequences were submitted to the BLASTn 2.2 search engine (Altschul et al., 1997) to obtain putative phylogenetic assignments for each band. The obtained sequences, combined with appropriate known 16S rDNA sequences from the GenBank database, were aligned using ClustalX 1.83 phylogenetic software package (Thompson et al., 1997). A 630-bp region of the alignment containing data from all sequences was selected for further phylogenetic studies. This alignment file was used to create bootstrapped (n = 1,000) neighbor joining trees, which were visualized using Tree-View (Win32) 1.6.6 (http://taxonomy.zoology.gla.ac.uk/rod/rod.html).
A total of 12 sequences were submitted to the GenBank database and were assigned the accession numbers of EF158011–EF158022.
Principal Component Analysis
Factor analysis as a multivariate statistical method is used to find a small number of factors from a data set of many correlated variables. Factor analysis is a useful tool for extracting latent information or variables (principal components) such as underlying, but not directly observable relationships between variables. Thus, PCA allows for the identification of groups of variables that are interrelated via phenomena that cannot be directly observed. This is accomplished by assuming that any observed (manifest) variables are correlated with a small number of underlying phenomena, which cannot be measured directly (latent variables). Factor analysis is based on the mathematical model of the reduced factor analytical solution (Pearson, 1901). The original data matrix is decomposed into the product of a matrix of factor loadings and a matrix of factor scores plus a residual matrix. The residual matrix contains the part of variance of the data set that cannot be explained by common factors (e.g., analytical uncertainties or feature-own variances). On the basis of the correlation matrix, orthogonal factors are extracted solving an eigenvalue problem. In general, the number of extracted factors is less than the number of measured parameters. The dimensionality of the original data space can be decreased by means of factor analysis. After rotation of the factor-loading matrix, the factors can often be interpreted as origins or common sources (Harman, 1976; Kleinbaum et al., 1988). In this work, PCA were carried out on physicochemical factors (i.e., pH, air and litter temperature, litter moisture, and relative humidity) to determine the most important factor(s) affecting the spatial diversity of microbial community in poultry litters.
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RESULTS AND DISCUSSION |
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TOPABSTRACTINTRODUCTIONMATERIALS AND METHODSRESULTS AND DISCUSSIONREFERENCES |
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) of the poultry house to see if any of these physical parameters would be factors affecting microbial diversity in poultry litter. We found that the litter temperature of the back areas (average temperature = 33.7°C; P <0.05) was higher than the other areas of the poultry house (Table 1). The waterer/feeder areas had the lowest average pH value of 8.2 (P <0.05) and the highest average moisture content at 51.0% (P <0.05; Table 1). All regions of the poultry house showed similar values for air temperature and relative humidity. The values for these physical parameters were similar to other findings (Gay et al., 2006; Miles et al., 2006).
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) revealed distinct poultry litter bacterial community structures within different areas of the poultry house. Using UPGMA analysis, the DGGE fingerprint patterns formed 2 major, well-supported (cophenetic correlation values 
82) clusters, one containing all of the waterer/ feeder samples (Figure 2, cluster A) and the second containing the grid sampling sites (Figure 2, cluster B). Cluster A contained 2 unique DGGE bands (bands 8 and 9) not found in the rest of the poultry house, whereas 3 bands that were present in the DGGE fingerprints from the rest of the house (bands 5, 10, and 12), were absent. The waterer/feeder samples of cluster A also contained the highest number of distinctive bands as compared with fingerprints from the rest of the poultry house (cluster B), suggesting a more diverse bacterial community in the higher moisture and higher traffic areas. Cluster B DGGE fingerprints, which belong to the grid samples, consisted of 2 distinct subclusters. The first subcluster, which included samples only found at the back of the poultry house next to the exhaust fans (Figure 2, B samples), formed a very well supported cluster (cophenetic correlation value of 93). The second subcluster included samples taken from the front, middle-front, and middle-back areas of the poultry house (Figure 2), with no discernible clustering pattern based on position within the house between these grid samples. The DGGE analyses have been used previously to monitor the change in aquatic microbial communities affected by poultry litter runoff (Ringbauer et al., 2006) and to monitor changes in the poultry littler microbial communities during the fertilization process (Enticknap et al., 2006), but to our knowledge, this is the first study using DGGE to determine the spatial variability of the poultry litter microbial community within a single poultry house.
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) were cloned and subjected to phylogenetic analysis. Alignment of cloned DGGE band sequences with those of organisms submitted to the GenBank database (Benson et al., 2005) showed that the DGGE band sequences clustered with 2 major phylogenetic groups, encompassing both low-GC (Bacillales and Lactobacillales) and high-GC (Actinomycetales) gram-positive bacteria (Figure 3). Our sequence analyses data are similar to those of Lu et al. (2003b), in which they reported that low-GC gram positive bacterial groups made up of about 62% of total 16S rDNA clones from wood-shaving poultry litter samples compared with 67% for our findings. In addition, the authors found that high-GC gram-positive bacteria comprised about 25% of the total clones compared with 33% for our study. The 3 major phylogenetic groups (Bacillales, Lactobacillales, and Actinomycetes) found in this study also corroborated well with other broiler chicken intestinal (Lu et al., 2003b) and litter (Martin et al., 1998; Fries et al., 2005, Enticknap et al., 2006) studies. No sequences from prominent DGGE bands were found to be similar to gram-negative bacteria, which was not surprising because gram-positive bacteria are known to dominant poultry litter communities, with gram-negative bacteria accounting for between 13% (Lu et al., 2003b, Fries et al., 2005) to 0% (Martin et al., 1998; Enticknap et al., 2006) of the bacterial community from fresh litter. Pathogenic strains of bacteria found in previous studies of broiler litter, including Bordetella sp., Clostridium sp. (Lu et al., 2003b), and Campylobacter spp. (Bull et al., 2006), were not found in the sequence analysis of our DGGE bands.
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). Of these 4 DGGE bands, Brachybacterium sp. and Arthrobacter sp. were found to be dominant community members in all poultry litter samples (Figure 2, band 2 and band 11). This is understandable because Actinomycetes are ubiquitous, especially in soil systems (Madigan et al., 1997) and have been found to be prevalent components in poultry litter (Martin et al., 1998, Lu et al., 2003b, Fries et al., 2005). These bacteria are rod-shaped to filamentous, aerobic, and generally nonmotile in the vegetative phase. They have been known to decompose woods (Fu and Thayer, 1975; Thayer, 1976), chitins (Reguera and Leschine, 2001), herbicides, caffeine, nicotine, phenol, and other unusual organic compounds (Atlas and Bartha, 1981; Madigan et al., 1997). The main genera of these Actinomycetes are Corynebacterium and Arthrobacter, both of which are known to be resistant to desiccation and starvation even though they do not form spores or other resting cells (Madigan et al., 1997). Specifically, Arthrobacter is a heterogeneous group that has considerable nutritional versatility. Thus, it is not surprising that these Actinomycetes should survive well in wood-shaving poultry litter environment.
Three of the 5 dominant bands found in all of the poultry samples contained sequences matching low-GC gram-positive bacteria (Lactobacillales and Bacillales) with 1 matching 99% to Lactobacillus sp. (Figure 2, band 1) and the other 2 matching 97% to Salinococcus sp. (Figure 2, band 3 and band 4). These 2 low-GC genera have been previously found to dominate poultry ileum (Lu et al., 2003a) and litter (Lu et al., 2003b) bacterial communities. Lactobacillales tended to predominate in the waterer/ feeder areas, possessing 2 unique bands (Figure 2, band 8 and 9) that were not found throughout the rest of the poultry house. Sequences from these 2 bands were found to be 99% similar to Atopostipes suicloacalis strains (Figure 3), a nonspore-forming facultatively anaerobic organism isolated from an underground swine manure storage pit (Cotta et al., 2004). These waterer/feeder areas are considered to have high moisture content (average about 50 vs. 30% for the rest of the poultry house) and low pH (average 8.2 vs. 8.4 to 8.6 for the rest of the house; Table 1). Lactobacillales, also called lactic acid bacteria based on their ability to produce lactic acid via fermentation (Madigan et al., 1997), are typically more resistant to acidic conditions and being able to grow well at low pH (around 4 to 5). Even though the pH of the waterer/feeder area litter was much higher than the optimum pH for growth of Lactobacillales, it has been reported that acidic conditions (pH = 5.5) can occur in waterer/feeder areas (Miles et al., 2006), which would be conducive to the dominance of these lactic acid bacteria within the litter bacterial communities.
A second unique set of DGGE bands (Figure 2, band 6 and 7) were present only in grid samples located at the back of the poultry house, where poultry litters are more dry and compact. Sequences from these bands identified them as low-GC gram positive bacteria, matching 97% to Streptococcus thermophilus (band 6) and 99% to Staphylococcus sp. (band 7) strain isolated from swine manure (Whitehead and Cotta, 2004; Figure 3). The presence of sequences matching these 2 organisms was not unexpected, given the fact that they have both been shown to constitute a minor portion of the poultry ileum (Lu et al., 2003a) and litter (Lu et al., 2003b) bacterial communities. The back areas of the poultry house appear to have the highest litter temperatures (average 33.5 vs. 31.7°C for the rest of the house) and lower moisture content, roughly 35% (Table 1). Both streptococci and staphylococci are facultative anaerobes that are able to produce lactic acid from lactose. In particular, staphylococci are relatively resistant to reduced water potential and tolerate dry and high salt conditions fairly well (Madigan et al., 1997). These conditions were observed in this study where the sodium concentrations from the poultry litters range from 11,000 to 16,000 mg per kg of poultry litter.
Principal Component Analysis of Physicochemical Parameters
Based on the fingerprint analysis (Figure 2), different bandings were observed for different areas of the poultry house. Therefore, PCA was carried out to extract the most important physical parameters affecting the diversity of the microbial community as observed from the DGGE bands. These physical parameters include the relative humidity, air temperature, litter temperature, pH, and moisture content of the poultry litters (n = 27). Statistica 7.0 (Statsoft, Tulsa, OK) was used to carry out principal component analysis to determine the main principal components from the original variables (Muller et al., 2001; Ogino et al., 2001; Van Der Gucht et al., 2001; Yang et al., 2001). Based on the eigenvalues scree plot (Figure 4), the original 5 physical parameters were reduced to 2 main factors (factor 1 and factor 2) from the leveling-off point(s) in the scree plot as suggested by Cattell (1966). The factor corresponding to the largest eigen value (1.46) accounts for approximately 51.5% of the total variance. The second factor corresponding to the second eigenvalue (1.02) accounts for approximately 31.5% of the total variance. The remaining 3 factors have eigenvalues of less than unity. The scree plot agrees well with the Kaiser criterion (Kaiser, 1960) where factors with an eigenvalue greater than unity would be retained for further analysis (in this case, 2 principal components were retained). Further analysis of factor loadings showed that moisture content and litter temperature were the 2 major factors affecting the diversity of the microbial community (Table 2). For factor 1, moisture has the highest factor loading value (0.903), which shows that moisture is the most influential variable for the first factor or principal component. For factor 2, litter temperature has the highest factor loading value (0.784), and pH is a second influential variable with factor loading value of 0.521. Factor loadings can be interpreted as the correlation between the factors and the variables (physical parameters).
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shows the cluster of sampling points (as affected by all 5 physical parameters). The cases (i.e., sampling points) that are clustered near each other have similar characteristics with respect to the factors. As can be seen from Figure 5, there are 5 distinct clusters when projecting all the cases (n = 27 sampling points) onto the factor plane. The middle front and middle back clusters are located toward the negative (left) side of this dimension—toward litter temperature, whereas the back and waterer/feeder clusters are located on the positive (right) side of the dimension—toward moisture content. Thus, it appears that litter temperature plays a major role in shaping the diversity of the microbial community toward the middle of the poultry house. Moisture, on the other hand, appears to play a major role in the microbial community structure in the back and waterer/feeder areas. The front cluster is more affected by moisture than litter temperature (e.g., sampling points from the front cluster are located on both sides of the dimension). There seems to be an overlap between the waterer/feeder cluster and the back cluster. Previous studies have shown that these areas exhibit similar physical properties (e.g., high moisture content, compacted litter layer that leads to caking; Gates et al., 1997; Miles et al., 2006). These areas contain the most diverse microbial community as demonstrated by the DNA fingerprinting analysis.
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Based on these analyses, it is clear that microbial diversity does exist at a microscale (i.e., within different regions of a poultry house). Environmental conditions vary at each location within the poultry house. These changes in environmental conditions do have a major effect on microbial dynamics, even at the microscale level. Many studies have shown that spatial scaling of microbial diversity does exist at the scale of a few centimeters (Harte et al., 1999; Green et al., 2004; Horner-Devine et al., 2004). For instance, Horner-Devine et al. (2004) found the existence of a taxa-area relationship for microorganisms in salt marsh sediments over an area of a few centimeters.
Although PCA may be a good tool in determining microbial diversity based on factor coordinates analysis, DGGE analysis is also necessary to effectively study spatial shifts in microbial diversity at the microscale level in a poultry house. The results from these microscale levels of analyses (e.g., understanding the major factors affecting microbial diversity) are a necessary first step in applying macroscale remediation options to reduce toxic air emissions and pathogenic incidence, whether on zone litter treatment or whole house treatment. Therefore, more experiments are needed to determine what fraction, if any, of these microorganisms is responsible for toxic air emission such as ammonia production or pathogenic incidence such as Salmonella or Campylobacter.
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ACKNOWLEDGMENTS |
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Received for publication February 1, 2007. Accepted for publication May 25, 2007.
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- Front samples; 
- Middle front samples; 
- Middle back samples; 
- Back samples; •- waterer/feeder samples.