introduction to water bacteriology
TRANSCRIPT
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Ruthie Jane P. Locayon, M.D., DPCP
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Is essential to support life No water, No Life
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Clear Colorless
Free from objectionable taste and odor
Must not contain: Any organisms
Chemicals
Radioactive materials
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Sewage Human or animal excreta
Other wastes Agricultural run-off water with pesticides
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Water is unsafe for human consumption whenit contains pathogenic and non-pathogenicorganism.
- WHO, 1993
Microbial contamination is still consideredthe most
critical risk factor in drinking waterquality.
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Food and waterborne diseases are amongthe most common causes of diarrhea.
Seventy percent of diarrhea due to food andwaterborne diseases have resulted fromingestion of contaminated food or water.
Diarrheal diseases for the past 20 years is thenumber one cause of morbidity and mortality,
incidence rate is high as 1,997 per 100,000population while mortality rate is 6.7 per100,000 population.
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Between 1988 and 1998, outbreak of FWBDsranks first (typhoid fever), second (cholera),fourth (food poisoning), sixth (hepatitis A),*and eight (diarrhea).
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1. Barrier approach involving treatment of
wastewater and raw water with disinfection,purification, etc.
2. Establishing allowable limits of indicators ofwater quality.
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Competence needed in the ability todemonstrate the presence and absence of aparticular organism/class of organism in agiven sample volume and provide an estimate
of their number.
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Outbreak investigation of waterborne disease Assessing safety, stability of water and water
products for public consumption.
Determining level of sanitation duringproduct preparation.
Regulatory compliance.
Incidence surveys
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Source water must be free from fecalcontamination.
Adequately treating fecal contaminated water.
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Bacteria Viruses
Protozoa
Helminths
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Salmonella Shigella
Escherichia coli
Vibrio cholera Campylobacter jejuni
Poliovirus, echovirus, Hepatitis Type A,Rotavirus, Norwalk virus
Giardia, Cryptosporidium, E. histolytica
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The methods of isolation and enumeration todetect the presence of many pathogens arecomplex and time-consuming
Detection of organisms normally present inthe feces of man and animals is used asindicator of excrement pollution in water.
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Indicates the presence of fecal materials. Possible presence of all relevant pathogens
Absence of fecal commensal organismsindicate that pathogens are probably alsoabsent.
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Indication of excrement pollution
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Always present when pathogenic organism ofconcern is present
And absent in clean uncontaminated water
Present in large numbers in the feces ofhumans and warm blooded animals
Easily isolated, identified and enumerated.
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Respond to environmental conditions andtreatment process similarly with othermicroorganisms
Ratio of indicator/pathogens should be high
Indicator and pathogens should come fromthe same source (gastrointestinal tract)
No organism fulfill all the criteria for anindicator organism butcoliform bacteriafulfill most.
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Easy to detect and enumerate in water Ability to ferment lactose in culture at 35C
Should not be detected in treated watersupply
Aerobic, facultative anaerobic
gram,-negative, non-spore forming
Rod-shaped
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E. coli most numerous Enterobacter
Klebsiella
Citrobacter False-positive results: coliforms from natural
aquatic flora and Aeromonas
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Subgroup of total coliform Ability to ferment lactose at 44C
Can be human or animal origin
Comprise the genus E. coli
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Normally found in human and animalintestines
Most reliable indicator of fecal contaminationin water.
Facultative anaerobe
Lactose-fermenting
Oxidase-negative
Gram-negative bacilli, motile
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Broad group which include: Pathogens and non-pathogens
Opportunistic microorganisms
Indicate general biological condition of
drinking water Supporting data on the significance of
coliform test results
Efficiency of various treatment process
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Multiple Tube Fermentation Technique Presumptive Test
Lauryl Tryptose Broth
Positive result gas formation within 24-48 hours
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Multiple Tube Fermentation Technique Confirmed Test
BGLB gas formation within 24-48 hours
EC gas formation within 24 hours or less
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Multiple Tube Fermentation Technique Completed Test
Single strength Lauryl Tryptose Broth
Completed result gas formation
LES Endo/MacConkey agar Gram staining gram-negative bacteria
(Lawrence Experimental Station )
(LES) formula
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The number of positive findings of coliformgroup organisms resulting from multiple-formation decimal dilution plantings
Estimates the density of coliforms in the
sample
Index of the number of coliform bacteria.
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Inoculate 20 ml water sample to 5 LTB
35C for 24-48 H
Presumptive testRecord no. of (+) tubes
44C water bath also for 24 hours
35C water bath also for 24-48H
Confirmatory test
Record no. of (+) tubes
EC(+) and BGLB(+) =(+) completed test
Completed test
Gram stain
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No. of positivetubes MPNindex/100ml Lower limit Upper limit0 8.0
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Total Coliform
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Sample container Made of glass or plastic (pre-sterilized)
Wide-mouthed
Use 120 ml clear bottle
Add 0.1 ml 3% sodium thiosulfate for chlorinatedwater sample
Volume of sample: Required volume should not be less than 100 ml
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Clean the tap Open the tap/pump outlet
Wipe using clean cloth or cotton swab
After cleaning the tap, flush for 1-2 minutes
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Sterilize the tap Close the tap or pump outlet and sterilize by
flaming with ignited cotton swab.
NOTE: For plastic tap, sterilize with cotton soaked
with cotton swab soaked in chlorox or 100 mg/Lsodium hypochlorite solution
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Flush the tap Open the tap and allow water to flow for 1-2
minutes.
Maintain normal pumping of water when sampling
hand pumps.
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Open the sterilized sampling bottle Untie the string of the protective paper cover and
unscrew cap.
Hold the cap with the protective paper cover facing
downward to avoid contamination.
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Fill the bottle Fill the bottle, avoid touching the mouth of the
bottle to the tap during filling.
Fill the bottle up the shoulder or leave at least 2.5
cm air space to facilitate mixing by shaking prior toanalysis.
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Cap the bottle Tightly screw the cap together with the protective
paper cover on the bottle.
Secure cover with string.
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Label the bottle Write the data and time of sampling, name of
collector, water sampling point code on a maskingtape.
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Store the bottle Place the sampling bottle in a cooler with ice or ice
gel pack.
Do not submerge the bottle in ice water during
storage and transport.
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Transport the water sample to the examiningwater laboratory immediately within 6 hoursafter collection or within 24 hours aftercollection under proper storage condition
(stored in an ice chest/box with sufficient iceor ice gel pack.)
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Heterotrophic plate count Formerly Standard Plate count
Procedure for estimating the number of liveheterotrophic bacteria in water.
Measures changes during water treatment anddistribution or in swimming pools
Employed as indicators of the proper functioning ofprocess and thereby as indirect indicators of watersafety.
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Heterotrophic plate count As a measure of numbers of re-growth (growth
following drinking water treatment)that may or maynot have sanitary significance.
Measure of possible interference with coliformmeasurements in lactose-based culture methods.
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Heterotrophic plate count Pour Plate Method
Simple to perform
Can accommodate volumes of sample or diluted
sample ranging from 0.1 to 2.0 ml. Colonies produced are relatively small and compact.
Media used R2A and NWRI agar.
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Heterotrophic plate count Quebec ColonyCounter used Spread Plate Method
Limited by the small volume of sample or diluted
sample that can be absorbed by the agar. To use this procedure, maintain a supply of suitable
pre-dried absorbent agar plates.
Media used R2A and NWRI agar.
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Membrane filter technique added expense ofthe membrane filter Benefits:
Concentration of larger samples on a membrane filter
is a key benefit over the MPN and Pour Plate andSpread Plate Technique.
Highly reproducible
Usually yields numerical results more rapidly thanMTFT.
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Membrane filter technique Uses:
Used by water treatment plants to monitor drinking,waste and surface water for the presence of coliformbacteria and E.coli
Used for microbial monitoring to the followingindustries.
Pharmaceutical
Cosmetics
Electronics
Food and beverage
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Membrane filter technique Advantages:
Permits testing of large sample volumes (of low turbiditywater)
Reduces preparation time as compared to many traditional
methods. Allows isolation and enumeration of discreet colonies of
bacteria.
Provides presence or absence information within 24 hours
Effective and acceptable technique. Used to monitor drinking
water in government laboratories. Useful for bacterial monitoring in the pharmaceutical,
cosmetics, electronics and food beverage industries.
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Membrane filter technique Procedure:
Collect the sample and make any necessary dilutions.
Flame the forceps and remove the membrane filter intothe funnel assembly.
Flame the pouring lip of the sample container and pourthe sample into the tunnel.
Turn on the vacuum and allow the sample to drawcompletely through the filter.
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Membrane filter technique Procedure:
Rinse funnel with sterile buffered water. Turn onvacuum and allow the liquid to draw completelythrough the filter.
Flame the forceps and remove the membrane filterfrom the funnel.
Place the membrane filter into the prepared Petri dish.
Incubate the proper temperature and for the
appropriate time period. Count the colonies under 10-15x magnification.
Confirm the colonies. (ID)
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Enzyme substrate coliform test (Chromogenicsubstrate test)
Principle: Total coliform bacteria
Chromogenic substrate Ortho-nitrophenyl--D-galactopyranoside (ONPG) or chlorophenol-red -D-galactopyrasonide (CPRG) detects enyme -D-galactosidaseproduced by coliforms
Fecal coliform (E. coli)
Fluorogenic substrate 4 methylumbelliferyl--D-
glucoronide (MUG) detects enyme -glucoronidase producedby fecal coliforms
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Enzyme substrate coliform test (Chromogenicsubstrate test)
Principle: Colorless: negative
Yellow: Total Coliforms Yellow Fluorescence: E. coli
May be quantified in Quanti Tray.
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A. MULTIPLE TUBE FERMENTATION TECHNIQUEInoculate 5 tubes of 10ml LSB triplestrength, 10 ml with 20 ml water sample
Incubate at 35C for 24 hours
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B. AQUA HETEROTROPHIC COUNT PLATE
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A. MULTIPLE TUBE FERMENTATION TECHNIQUE1. Look for gas production in LSB
if + inoculate BGLB incubate at 35C for 24hrs
inoculate EC incubate at 44C for 24hrs
if - re-incubate for another 24hrs
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B. AQUA HETEROTROPHIC COUNT PLATE1. Count number of coloniesinterpret
2. End of exercise
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A. MULTIPLE TUBE FERMENTATION TECHNIQUE1. Read LSB that were negative after 24 hrs and is + after
48hrs
if + inoculate BGLB and EC
if - discard end of procedure
2. Read BGLB ( from + LSB on Day 2 after 24 hrs incubation)
if + inoculate Mac Conkey incubate at 35C for 24hrs
if - reincubate
3. Read EC (from + LSB on Day 2 after 24 hrs incubation)
if + positive for fecal coliformsif - absence of fecal coliforms
Discard EC after reading
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1. Read MacConkey for colored colonies ( from BGLB after24hrs)
if + inoculate LSB single strength and incubate for
24-48hrs
inoculate TSA slant and incubate
if - discard
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2. Those inoculated from LSB after 48hrsRead BGLB ( after 48 hrs incubation)
if + inoculate Mac Conkey incubate at 35C for 24 hrs
if - discard
Read EC
if + positive for fecal coliforms
if - absence of fecal coliforms
if BGLB and EC are negative END OF PROCEDURE
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1. From MacConkey (from BGLB after 24hrs)Read LSB single strength and incubate for another 24hrsif negative
if + positive for coliforms
if - no coliforms
From TSA SlantDo gram stain and look for gram negative bacilli2. Read MacConkey for colored colonies ( from BGLB after48hrs)
if + inoculate LSB single strength and incubate for
24-48hrs
inoculate TSA slant and incubate
if - discard
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1. From MacConkey (from BGLB after 48hrs)Read LSB single strength and incubate for another 24hrsif negative
if + positive for coliforms
if - no coliforms
From TSA SlantDo gram stain and look for gram negative bacilli
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Group WaterSource Presumptivetestof+tubes
Confirmatorytest of+ tubesMPN Completed Test Remarks
BGLB
EC BGLB EC MC LTB
1 1 5 5 0 >8.0 + + Unsafe