Dr. Jason Woodworth - What Can We Do In Feed Processing To Reduce Risk
ย
Thesis presentation - Yaeli Etstein
1.
2.
3. Future ?
E. coli Enterococcus faecalis
EC 2006**
E. Coli (500/100mL) Feacal enterococci (200/100mL)
USEPA 1986*
Escherichia coli (235/100mL) Feacal enterococci (104/100mL)
EEC 1975
Total coliform (10,000/100mL) Feacal coliform (2,000/100mL) Feacal streptococci (100/100mL)
* Based on Geometric mean
** Based on 95% evaluation
4. ๏ The most common enterococci in human feces (90-95%)
๏ Responsible for the majority of human enterococcal
infections
๏ High endogenous resistance to stressful
conditions by activating the VBNC state
๏ High ability to acquire and transfer rapidly
various resistance genes
5. (EPA 1600)
37 ยฑ 0.5ยฐC 24h
โข Long incubation time
โข Underestimating methodologies:
1. VBNC bacteria are not counted
2. Heterogenic distribution (plates)
3. Neighboring colonies dynamics (plates)
8. Gene
selection
โข Scientific literature
โข Database search and analysis (NCBI, RDP etc.)
QPCR
system
design
โข Short amplicons (50-150bp)
โข Dimers and steady structures formation
โข Hair pin loops and amplicon mfold
โข Base pair composition โ Tm adjustment and fluorophore quenching
Systemsโ
screening
โข Specificity tests
Accuracy and
precision
โขSpiking sterile seawater samples with known quantities of bacteria
โขEnvironmental samples processing and comparison with the standard methodsโ quantification
Protocol
development
โข Concentrating bacteria from seawater
โข DNA extraction
โข Removal of inhibitory substances and PCR inhibition control
โข Dead bacteria screening
High efficiency and sensitivity
9. Species
Amplification
16s rDNA PBP5 GroES
Phylum "Firmicutesโ
Class "Bacilli"
Order "Lactobacillales"
Genus Enterococcus
E. faecalis V583 + + +
E. faecalis 14506 + + +
E. faecalis 2020 + + +
E. faecalis 29212 + + +
E. faecalis F76-117 + + +
Genus Enterococcus E. faecium ISO - - -
E. faecium 180 - - -
Order "Lactobacillales" Aerococcus viridans - - -
Class "Bacilli" Bacillus sp. - - -
Staphylococcus aureus - - -
Staphylococcus epidermidis - - -
Gastrointestinal and water
quality standard bacteria
E. coli K12 MG1655 - - -
E. coli K12 Hfr - - -
E. coli 8A - - -
E. coli 7L - - -
E. coli 7G - - -
E. coli environmental isolate - - -
Gastrointestinal bacteria Shigella soneii + + +
Salmonella enterica - - -
Citrobacter freundii - - -
Serratia marcescens - - -
Enterobacter cloaca - - -
Klebsiella oxytoca - - -
Marine bacteria Seawater isolate #1-3 - - -
Env. Vibrio sp. #1, #4 and #5 - - -
Vibrio shiloi - - -
Vibrio corallilyticus - - -
Vibrio harveyi CM18 - - -
Vibrio harveyi CM19 - - -
Vibrio harveyi CM32 - - -
Vibrio harveyi CM37 - - -
10. 16s rDNA PBP5GroES
Amplification
without
E. faecalis
genomic DNA
Amplification
with ~3000
E. faecalis
Genomic
units/well
E. coli
S. aureus
Bacillus sp.
V. corallilyticus
V. Shiloi
Vibrio #1
SW #1
SW #2
11. The addition of the TaqMan probe resulted with 100%
specificity against the 36 tested strains
Small amount of target DNA is sufficient to eliminate the
production of all non-specific PCR products
The use of 3 amplification systems lowers the odds to
encounter another bacterium that have all sequences of
primers and probes placed in the same manner in its
genome
16. F(3,64)=0.83, P=0.48
One way ANOVA
No significant
difference
'between
methods
quantification
Contaminated
Contaminated
Non-
contaminated
Non-
contaminated
Contaminated
Contaminated
Non-
contaminated
Non-
contaminated
Different
French
beaches
QPCRMPN
17. ๏ Molecular techniques, specifically nucleic acid amplification
procedures, provide sensitive, rapid and quantitative analytical
tools for the detection of specific organisms.
๏ Factor contributing for qPCR robustness:
- Detailed design of each amplification system
- Optimization of the full protocol
๏ Fundamental differences between amplification systems have
led for the design of a system-specific internal control.
18. Professor Adam Friedmann
Itay Kilovaty
Alon Daya
Dr. Tzachi Bar
Tal Amit
Marina Schetman
Professor Stella Mitrani-Rosenbaum
Enterococci are a subgroup within the fecal streptococcus group. Enterococci are distinguished by their ability to survive in salt water, and in this respect they more closely mimic many pathogens than do the other indicators. Enterococci are typically more human-specific than the larger fecal streptococcus group. EPA recommends enterococci as the best indicator of health risk in salt water used for recreation and as a useful indicator in fresh water as well. (http://water.epa.gov/type/rsl/monitoring/vms511.cfm)
Studies conducted by EPA to determine the correlation between different bacterial indicators and the occurrence of digestive system illness at swimming beaches suggest that the best indicators of health risk from recreational water contact in fresh water areย E. coliย and enterococci. For salt water, enterococci are the best. Interestingly, fecal coliforms as a group were determined to be a poor indicator of the risk of digestive system illness. However, many states continue to use fecal coliforms as their primary health risk indicator.
ืืืจืฅ ืืืืจื"ื ืืืืืืงืื ืืขืืงืจืืื ืฉืื ืืืจืื ืืืืืงืืช ืืืืืช ืื ืื ืืืืคื ืจืืฆื ืื ืื ืชืจืืงืืงืื (ืืงืกื ืขื ืชืืฆืืืช ื ืืืืจ ื ืืืืืจ-ืืฆืืืจ 2012).
ืืืื ืืฉ ืืขืืจ ืืฉืืืืช ืืืฉืืช โ ืืืืงืืืจืืืช ืฉืื ืืืืจืืช ืืืชืจ, ืืืืืงืืช ืืืชืจ ืืจืืืฉืืช ืืืชืจ ืืืืืืช ืืืืืงืื ืืืืืืืช ืกืืืืชืืืช, ืืืื, ืงืืื ืืืช ืืื ื ืืฆืื ืืช ืืฉืืื ืื ืคืืฆื ืืืืชืจ ืืืื โ ื-real-time PCR.
There are two basic methods for analyzing water samples for bacteria:
1. The membrane filtration method involves filtering several different-sized portions of the sample using filters with a standard diameter and pore size, placing each filter on a selective nutrient medium in a petri plate, incubating the plates at a specified temperature for a specified time period, and then counting the colonies that have grown on the filter. This method varies for different bacteria types (variations might include, for example, the nutrient medium type, the number and types of incubations, etc.).
2. The multiple-tube fermentation method involves adding specified quantities of the sample to tubes containing a nutrient broth, incubating the tubes at a specified temperature for a specified time period, and then looking for the development of gas and/or turbidity that the bacteria produce. The presence or absence of gas in each tube is used to calculate an index known as the Most Probable Number (MPN).
**Negative Plates result when the buffered rinse water (the water used to rinse down the sides of the filter funnel during filtration) has been filtered the same way as a sample. This is different from a field blank in that it contains reagents used in the rinse water. There should be no bacteria growth on the filter after incubation. It is used to detect laboratory bacteria contamination of the sample.
Positive Plates result when water known to contain bacteria (such as wastewater treatment plant influent) is filtered the same way as a sample. There should be plenty of bacteria growth on the filter after incubation. Positive plates are used to detect procedural errors or the presence of contaminants in the laboratory analysis that might inhibit bacteria growth.
**Lab Replicates. A lab replicate is a sample that is split into subsamples at the lab. Each subsample is then filtered and analyzed. Lab replicates are used to obtain an optimal number of bacteria colonies on filters for counting purposes. Usually, subsamples of 100, 10, and 1 milliliter (mL) are filtered to obtain bacteria colonies on the filter that can be reliably and accurately counted (usually between 20 and 80 colonies). The plate with the count between 20 and 80 colonies is selected for reporting the results, and the count is converted to colonies per 100 mL.
**Knowns. A predetermined quantity of dehydrated bacteria is added to the reagent water, which should result in a known result, within an acceptable margin of error.
**Outside Lab Analysis of Duplicate Samples. Either internal or external field duplicates can be analyzed at an independent lab. The results should be comparable to those obtained by the project lab.
ืฉืชื ืืื ืืงืืช ืฉืื ืืช: ืืืืช ื ืงืจืืช SYBRยฎ Green ืืืฉื ืืื TaqManยฎ probe
ืฉืชื ืืฉืืืืช ืืืืกืกืืช ืขื ืงืจืืืืช ืฉื ืกืืื ืืื ืคืืืจืืกื ืืื.
Allows the scientist to actually view the increase in the amount of DNA as it is being amplified.
Dye molecules can bind only to a double strand. DNA binding results in a dramatic increase of fluorescence signal. The resulting DNA-dye-complex absorbs blue light (ฮปmax = 488 nm) and emits green light (ฮปmax = 522 nm).
In summary, concentrations of E. faecalis measured with real-time PCR were highly correlated with those measured by plate and microscopy counts. The correlation was even stronger in the second spiking attempt, an assay performed with an E. faecalis inoculum of non-dividing cells (Avg. R2 of 0.95 versus 0.986).
The main challenge that arises from these assays is the accuracy level of the qPCR when seawater contains the concentration of bacteria set by the new criteria as the threshold for contamination. Further work must concentrate on the improvement of the DNA extraction procedure (not necessarily based on the protocol of the PowerWater kit), in terms of producing higher and constant DNA yields to gain better reproducibility , and in terms of simplification, to enable the implementation of the protocol with the same high efficiency in the work of different laboratories.
Molecular techniques, specifically nucleic acid amplification procedures, provide sensitive, rapid and quantitative analytical tools for the detection of specific organisms.
In this study I have shown that the two qPCR systems I developed and the third taken from the work of Santo-Domingo (ref 2003) perform better with environmental samples than seen in previous works and show very high levels of agreement with the standard methods regarding the level of seawater contamination. I attribute that to two main reasons: the detailed design of each amplification system and the optimization of the full protocol. The potential problematic issues that could come up from the combination of qPCR, with its innate limitations, and versatile marine samples have led to the parallel use of three amplification systems for the quantification of the same bacterium from seawater. Three amplification systems serve as back-ups to each other in case results will indicate the need to eliminate the use of one.
The use of multiple amplification systems brought to my attention that there are fundamental differences between individual systems because of their innate characteristics (amplicon size and base composition, primers Tm etc.). This notion prompted the development of a new internal control that is amplification system-specific and showed very promising results with a small number of seawater samples.