Sem 2 Practical

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    Safety in the labRULES, REGULATIONS AND CODE OF CONDUCT FOR SAFETY IN THE

    MICROBIOLOGY LABORATORY

    APROPRIATE PROTECTIVE CLOTHING MUST BE WORN IN THE

    LABORATORY AT ALL TIMES.

    SAFETY GLASSES TO BE WORN AT ALL TIMES.

    (LABORATORY COATS MUST BE WORN AT ALL TIMES AND MUST BE

    CLEAN AND FREE OF GRAFFITTI.)

    BEHAVIOUR IN THE LABORATORY MUST BE APPROPRIATE TO REFLECT

    SAFETY STANDARDS. (Performance and behaviour in the laboratory are taken

    into account for CA marks.)

    EATING, DRINKING AND SMOKING ARE NOT PERMITTED IN THE

    LABORATORY.

    HANDS MUST BE WASHED WITH SOAP ON ENTERING THE

    LABORATORY AND AT ALL TIMES LEAVING THE LABORATORY.

    BENCH TOPS MUST BE SWABBED WITH DISINFECTANT AT THE START

    AND END OF EACH CLASS. (ETHANOL IS PROVIDED)

    WASTE DISPOSAL BAGS ARE PROVIDED FOR PETRI DISHES AND

    OTHER DISPOSABLES WHICH REQUIRE AUTOCLAVING.

    WASTE DISPOSAL BINS ARE PROVIDED FOR WASTE PAPER .

    DISCARD JARS ON THE BENCH TOPS CONTAINING DISINFECTANT ARE

    PROVIDED FOR DISPOSAL OF GLASS SLIDES AND USED PIPETTES AND

    PIPETTE TIPS

    SINKS MUST NOT BE USED FOR WASTE DISPOSAL.

    HANDLE ALL CULTURES AS IF POTENTIALLY PATHOGENIC (i.e

    DANGEROUS DISEASE CAUSING ORGANISMS).

    HANDLE ALL MATERIAL I.E, WATER FROM RIVERS/LAKES etc., SOIL,

    SLUDGES AND MATERIALS FROM OTHER SOURCES AS CONTAINING

    POTENTIAL PATHOGENS.

    DO NOT LICK LABELS, PENCILS, FINGERS etc.

    TRY TO PREVENT RUBBING YOUR EYES AND LIPS, BE AWARE OF THE

    POSSIBILITY OF CONTAMINATION AT ALL TIMES.

    THINK ASEPTIC TECHNIQUE AT ALL TIMES

    IN CASE OF ACCIDENT (BREAKAGES, SPILLAGES etc.) INFORM THE

    LECTURER IMMEDIATELY.

    ALWAYS LEAVE THE LABORATORY CLEAN AND TIDY FOR YOUR NEXT

    CLASS. Clean bench top of stains and put away microscopes, hot plates etc.

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    Water MicrobiologyThe quality of water, for both drinking and recreation

    purposes, is now a matter of national and Internationalconcern. The European Commission has issued a councildirective relating to the quality of water supplies (TheDrinking Water Directive (80/778/EEC), 1980). A morerecent Directive relates to the quality of water intended forhuman consumption (98/83/EC)The Irish Government brought the original directive into lawby introducing the European Communities (Quality Of Water

    Intended For Human Consumption) Regulations,1988 whichare the statutory basis for protection of drinking water qualityin Ireland. The bodies charged with the implementation of theregulations are the sanitary authorities, which then furnish theresults to the EPA in order to publish the annual report ondrinking water quality.

    Officially approved methods for the bacteriologicalexamination of water are given by the UK Department ofHealth (DHSS, 1985) and in the USA by the AmericanPublic Health Association (APHA, 1986).

    In relation to public health the principal tests applied to waterare:-

    the viable plate count, and those for coliform bacteria, faecal coliform (E.coli), faecal enterococci and sulphite-reducing Clostridia.

    The viable plate count is carried out at 22C and 37C.

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    The terms used for the microorganisms may be defined asfollows:

    Coliform bacteriaare members of the Enterobacteriaceae andinclude the genera Citrobacter, Enterobacter,Escherichia, Hafnia, Klebsiella and Serratia.

    These grow at 37C and possess a -galactosidaseenzyme.Faecal coli, also known as thermotolerant colirefers to Escherichia coli, which grows andproduces indole at 44.5C.

    Faecal enterococci are members of the genusEnterococcus,and includeE. faecalis, E. faecium andE. durans andbelong to the family Streptococcaceae

    They grow at 10C and 45C, in the

    presence of 40% bile,

    6% NaCI, and on

    standard azide media, and

    hydrolyse aesculin.

    Sulphite-Reducing Clostridia refer to Clostridiumperfringens.

    These bacteria areGram positive rod shaped anaerobic, produce spores and reduce sulphite, blackening the medium

    which is characteristic and cause

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    stormey clot in litmus milk

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    Sampling.Water samples are usually collected using sterile 300 ml or500 ml bottles supplied by the laboratory.

    Plastic is replacing glass bottles because of concern aboutglass in food preparation and recreational areas.For samples of chlorinated water the bottles must containsodium thiosulphate (0.1 ml of a 1.8% solution per 100 mlcapacity) to neutralize chlorine.

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    Viable plate countsThese are required under EU Directives.

    Nutrient agar (Yeast extract agar) is used and tests are donein duplicate with undiluted and serially diluted samples. Oneset is incubated at 20-22C for 3 days and the other at 37Cfor 24-48 hours.

    Procedure:Prepare serial dilutions of sample from 100,10-1,10-2,10-3, usingthe diluent. (Use either Ringers or Peptone water).

    Observe aseptic technique throughout.

    Label two series of petri dishes, one for 22C and 37C induplicate.

    Starting with 10-3dil. carry out plate count using the pourplate technique and carry on with 10-2,10-1,100.

    Pipette 1 ml of sample into petri dishs in duplicate and addmolten ager.

    Mix agar and sample very carefullyto disperse the bacteria.

    NB(You have only one chance to do this as you cannot goback to undo the solid agar)

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    After incubation count the colonies carefully and calculate

    thenumber of CFU's perml of the original sample,using the dilution factors.

    Prepare a table showing the results.

    ***Why incubate at 37C ?***

    The target values are

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    Presumptive Coliform test:MPN method with MacConkey broth.

    Multiple Tube Method to determine Most Probable Numberof Coliforms.

    Select the range according to the expected purity ofthe water:

    Mains chlorinated water A andB

    Piped water, not chlorinated A, B and CDeep well or borehole A, B and CShallow well B, C andDNoinformation A, B, C andD

    A: 50 ml of water to 50 ml of double-strength broth.

    B: 10 ml of water to each of five tubes of 10 ml of double-

    strength broth.

    C: 1 ml of water to each of five tubes of 10 ml of single-strength broth.

    D: 0.1 ml of water to each of five tubes of 10 ml of single-strength broth.

    Question.Why are sample volumes C and Dusually omitted when sampling treatedmains water?

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    Procedure:

    You have on your bench in a test tube rack the series:

    five tubes of 10 ml of double-strength broth.

    Add 10 ml of sample to each.

    five tubes of 10 ml of single-strength broth.

    Add 1 ml of sample to each.

    five tubes of 10 ml of single-strength broth.

    Add 0.1 ml of sample to each.*************************************************Incubate at 35-37C and note the numbers of tubes showingacid and gas after 48 h.

    Tap any tubes showing no gas. A bubble may then form inthe Durham's tube.

    Consult the MPN tables and read the most

    probable number of presumptive coliform

    bacilli/100 ml of water. Report the results.

    Small amounts of gas occurring after 48 h inpresumptivetubes are disregarded unless the presence of coliformbacilli is confirmed by plating.

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    Confirmatory test.From each tube showing acid and gas, inoculate a tube ofMacConkey broth and a tube of peptone water.

    ****Incubate these at 44.5C for 24 h in a reliable water-bath(Eijkman test) along with controls of known strains ofE. coli (which grows at 44.5C) and K. aerogenes(which does not).

    Plate also from positive tubes on MacConkey agar, EosineMethylene Blue (EMB) and nutrient agar.

    Observe gas formation at 44.5C and test the peptone-water culture for indole.

    Do Gram stain and oxidase test on growth from nutrientagar.

    Should find Gram negative, non sporeforming and oxidase negative cultures.

    OnlyE. coli produces acid, gasand indole at 44.5C.

    Read the most probable numbers of E.

    coli ('faecal coliform') from Tables and

    report the results.

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    Questions.What are the components of the MacConkey broth?

    What is the Carbon and energy source in themedium?How does this medium encourage the growth ofcoliforms?What is the gas in the Durham tube composed ofand where does it come from?

    Remember that the organisms cultured from any positive37C tube and grown at 44C represent coliforms culturedfrom the volume of water placed in the 37C tube.For example:

    50 ml 10 m1 1 ml MPN/100 ml

    Tubes positive at 37 C 1 2 2 10presumptive coli

    Tubes positive at 44.5 C 1 1 0 3 ..E. coli

    For further investigation, subculture colonies from theMacConkey/EMB plate for biochemical tests, e.g. with anAPI kit or the IMViC test.

    The IMViC (I = indole, M = methyl red, V = Voges-Proskauer, C = Citrate)tests are not routinely used in water microbiology.

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    ***Acid and gas in MacConkey broth, may occasionally bedue to spore formers. e.g. Cl. perfringensat both 37C and44C.

    Question.However, these organisms do not

    grow on the MacConkey or EMB

    plates.

    Explain why?

    Most raw waters showing acid and gas do in fact containcoliform bacilli, but in about 5% of chlorinated waters acidand gas are caused by C. perfringens.

    The target levels for coliforms andE.coli are absence

    from 100 ml.

    IMViC testI = indole production from tryptophan,M = methyl red, indicates acid production from glucose,V = Voges-Proskauer, indicates neutral end products from glucose i.e. Acetylmethyl carbinol,C = Citrate utilization by the suspect culture

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    Coliform test: membrane filter method

    Advantages of using membrane filter techniques for

    waters(1) Speed of obtaining results.

    (2) Saving of labour, media, glass and cost of materials if thefilter is washed and re-used.

    (3) Sample can be filtered on site, if the filter is placed ontransport medium and posted to the laboratory, thus avoiding

    delay in transporting the sample.

    (4) Organisms can very easily be exposed to pre-enrichmentmedia for a short time at an advantageous temperature.

    Disadvantages of using membrane filter techniques for

    waters

    (l)There is no indication of gas production (some waterscontain large numbers of non-gas producing lactosefermenters capable of growth in the medium).

    (2)Membrane filtration is unsuitable for waters with highturbidity and low counts because the filter will becomeblocked before sufficient water can pass through it and

    (3)Large numbers of non-coliform organisms capable ofgrowing on the medium may interfere with coliform growth.

    If large numbers of water samples are to be examined andmuch field work is involved the membrane method isundoubtedly the most convenient.

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    Procedure:Set up the membrane filtration unit as demonstrated.

    Prime the membrane by passing approx. 20 ml of sterilewater through.

    Pass two separate l00-ml volumes of the water samplethrough 47-mm diameter membrane filters.

    Question.

    What is thepore sizeof the

    membrane you are using?

    ****If the supply is known or is expected to contain morethan l00 coliform bacilli/l00 ml, use l0 ml of water

    diluted with 90 ml of quarter-strength Ringer's solution.

    Place sterile absorbent pads in sterile petri dishes andpipette 2.5-3 ml of m Endo broth over the surface andallow to absorb.

    Place amembrane face up on each pad.

    Incubate one membrane at 44.5C and one at 37C for48h.

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    Counting and reporting results.

    Count the typical colonies only and report

    aspresumptive coliform andE. coli/l00 mlof water.

    Cl. perfringes does not grow.

    Completed test

    Several colonies from the membrane are subcultured intolactose broth fermentation tubes and on a nutrient agarslope.

    Both are incubated at 35C for 24 h.

    Gas in the broth and a Gram-negative non-sporing rod onthe slope is evidence of coliform bacilli.

    Gram stain the culture and carry out the OXIDASE TEST.

    For the oxidation of glucose many bacteriautilize a respiratory transport chain, a

    collection ofcytochromesand other enzymesterminating incytochromes oxidase. Bacteria

    producing cytochromes oxidase can oxidase thesubstratetetramethyl- para-phenylene diaminehydrochloride, the oxidase reagent, which isoxidised to produce an intensely colouredpurple product in about 10 seconds.

    Follow the instructions of your demonstrator whencarrying out the Oxidase test.

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    4-Methyl umbelliferyl--D-gluconate (MUG)

    may be added to the tryptone water to give an

    additional test for, -glucuronidase activitywhich is positive only for E.coli (ca.90% of

    strains) and some shigellas.

    MUG is hydrolysed to give a fluorescent

    compound, detected by exposure to UV light.

    The indole reagent may then be added.

    Questions

    How many bacteria were in the water sample?

    How many of these bacteria were total

    coliforms?

    How many were faecal coliforms?

    Explain the significance of these results.

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    Faecal Enterococci in water

    These organisms are useful indicators when doubtful resultsare obtained in the coliform test. They are more resistant thanE. coli to chlorine and are therefore useful when testingrepaired mains. Group D streptococci only are significant.This group of microorganisms were known as faecal

    Streptococci, but are now referred to as Enterococci.

    MPN method.

    Use one of the azide broths, e.g. azide glucose broth orEnterococcus Presumptive Broth.

    Add 50 ml of water to 50 ml of double-strength medium.

    Add 10 ml of water to each of five tubes of 10 ml ofdouble-strength broth.

    Add 1 ml of water to each of five tubes of 5 ml of single-strength broth.

    Incubate at 37C for 48/72 h.

    Subculture any tubes showing acid production to tubes ofsingle-strength medium and incubate at 44.5C for 18/24 h.

    Record tubes showing acid and

    consult the MPN tables.

    Present the results in a table.

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    Subculture each presumptive positive tube to ethylviolet azide broth and incubate at 44.5C for 24-48 h.Turbidity and a purple-stained button of growth at the

    bottom of the tube indicate enterococci.

    Confirm by microscopic examination for short-chainstreptococci.

    Report your results in a table.

    Questions

    What are the components of the

    medium used in the MPN method?

    Why is azide used in the medium,

    give an explanation?

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    Membrane method

    Pass l00 ml of water through a membrane filterpreviously primed with sterile water, and place the filter

    on a plate of membrane enterococcus agar.

    Incubate at 44.5C for 48/72 h.

    All red or maroon colonies are presumptive positives.

    Carefully remove the filter and place colony-side down

    onto a plate of aesculin bile agar to imprint the colonies.

    Incubate at 37C for 12 h. A black zone appears undercolonies of faecal enterococci.

    Carry out the catalase test.

    The target level for faecal enterococci isabsence from 100 ml.

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    Sulphite-reducing clostridia

    MPN method

    Heat the sample to 75C in a water-bath and hold it at thistemperature for 10 min.

    Culture as follows in Differential Reinforced Clostridiamedium.Add 50 ml of the sample to a 50 ml bottle of double strengthmedium,10 ml to each of five 10 ml tubes of double strength medium,

    and1 ml to each of five l0 ml tubes of single strength medium.

    Overlay each medium with sterile mineral oil (2 cm deep) toexclude as much air as possible.

    Questions.

    Why is the water sample preheated beforethe analysis is carried out?

    Why are the samples overlayed with oil,

    explain the reason?

    What makes the medium differential for

    Clostridium?

    Explain the black stain in the medium.

    Cap and incubate at 37C for 48h.

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    Tubes showing blackening are presumptive positives butother clostridia may give this reaction.

    Confirm by subculture in litmus milk medium.

    Incubate at 37C overnight andrecord tubes showing stormyclot fermentation.

    Explain what the stormy clot reaction

    is?

    Carry out a spore stain.

    Consult the MPN tables and report

    results in table form.

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    Membrane method.

    Prime the filter in the usual manner.

    Pass 100 ml of the heated sample through a 47 mm, 0.45 mfilter.

    Place the filter face downwards on the surface of BismuthSulphite agar.

    Pour 20 ml of the same medium, cooled to 50C, over thesurface and when this has solidified incubate the plates at

    44C anaerobically.

    Count the black colonies with haloes. These are probablyClostridium perfringens.If too many are present all the medium will be blackened.

    ****The target levels for Cl. perfringes

    are < 20 per ml.

    Report results in your manual.

    What are the ingredients of the Bismuth

    Sulphite agar?

    MPN Tables here

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    HYGIENE MICROBIOLOGY.

    Asses sin g Microbiologic al Quality: Person al

    Hygiene

    !ur"aces Air an# Pro#uct$Materials%

    Per so n al Hygi en eA si&'le &et (o# o" as sess ing )ac te ri ologi cal *uality o"

    (an #s +an in#ication o" 'erson al (ygien e, is to ta- e

    contact "inger 'rints on t(e sur"ace o" agar 'lates %

    .(is &ay be use# to e/alua te t(e e""iciency o" (an#

    as (in g 'roc e# u r es or to e/ al ua t e t( e e""icti/ en e s s o"

    #isin"ectants an# (an# as( solut ions%

    Method:

    Agar Me#iu&: .!A Mannitol !alt Mcon-ey%

    learly &ar - out on t(e bac- o" t (e ag ar 'lat e t(e ar ea s

    onto (ic( t(e "ingers are to be 'lace#%

    .a-e .o agar 'lates%

    abel one 'late b e or e ! as h in g " an# t(e secon# onea ter ! ash i ng" %

    are"ully i&'rint eac( "inger onto t(e agar 'late

    maintaining contact #or three seconds.

    as( your (an #s an# #ry t(e & an# re' ea t "or t(e sa &e

    (an# on t(e secon# 'la te %

    abel an# incubate 3724$48 (rs%

    A"te r incubat ion re'or t on t(e nu&bers o" s 'er (an#

    an# assess t(e e""ec t o" (an# as(ing%

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    #$ra%es ..(e bac teriological *ua li ty o" sur"aces can be assesse# by

    using ag ar cont ac t 'lat es +o# ac 'lat es , or by using a

    sabbing tec(ni*ue%

    Conta% t &l ate s .

    ontac t 'lat es a re 'oure# using t(e &ol ten agar su''li e# %

    .!A Mannitol sal t Mcon-ey agar an# !abarou# e;trose

    agar%

    13 &l o" &ol ten agar is care"u lly 'oure# into t(e agar 'la te

    an# alloe# to set%

    .(e a ga r 'lat es ar e us e# to ta- e an i&'rin t o" t( e sur" ac e

    un#er e;a&ination incubat e# t(e a''ro'riat ete &' e r a t u r e an # e; a&i n e# %

    e'ort your resul ts%

    #!abs

    .e&'lates outlining an area o" 5 c& 2 are "irst sterili

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    'ir 'nalysi s.Some of the devices and methods used in the bacteriological analysis ofair are as follows:-Casella Slittoagar sampler;

    Anderson Two Stage Sampler;Biotest Centrifugal Air Sampler;Hawksley FilterSurface Air Sampler (SAS)Settle Plates.

    The Casella Slittoagar sampler is set up as demonstrated.Air is sampled through the slits and impactedonto the surface of a plateof TSA to collect bacteria and Sabaroud Dextrose Agar to collect yeasts

    and moulds.After incubation at the appropriate temperatures, CFUs are counted andreported as CFUs per m3air sampled.

    Q? What temperature should you incubate to recover:Bacteria_____________Yeasts/moulds_____________

    Table showing flow rate and volume of air sampled using variousslits in the Casella sample.No. of slits Flow/Min (litres) Time of one cycle in

    Min.

    Volume sampled

    (litres)1 175 0.5

    25

    87.5

    350875

    2 350 0.525

    1757001750

    3 525 0.525

    262.510502625

    4 700 0.52

    5

    3501400

    3500

    Anderson Two Stage Sampler

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    The instrument is set up as demonstrated.

    Particles carrying microorganisms are impactedonto the surface of agar

    media and incubated to allow growth to occur.The upper chamber collects all the non respirable particles (>8.0m ) and

    the lower chamber collects respirable particles (around 4 m diam.).The pump maintains a flow rate of 28.3 liters/min.

    Use two plates ofTSAto recover _________________incubate at what _____C for________hrs

    Mannitol Salt agarto recover __________________ incubate at what _____C for________hrs

    Sabaroud Dextrose agar to recover ________________________ incubateat what C for ________hrs

    Sample the air for four minutes.

    Determine volume of air sampled in m3.________________

    After incubation report your results as CFUs per m3of air sampled.

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    Biotest Centrifugal Air Sampler

    The agar strips are carefully inserted into the device as demonstrated.The sampler is placed into position and turned on for 4mins.

    After sampling the strips are placed into their plastic containers andlabelled and incubated as appropriate.Agar strips contain agar to recover bacteria and Yeasts and moulds.

    ount t(e coloni es on t(e aga r stri' a"t er incuba ti on an#

    calculate as "ollos:

    The number of organisms per unit of air volume can be calculated as

    follows:-

    CFU/m3= Colonies on the agar strip x 25Sampling time (mins)

    Settle Plates.This method allows particle carrying microorganisms to sediment out

    onto the surface of an open petri dish.Open the lids of agar media to the air and close lids after 10 mins and 30mins and 60 mins.

    Carry out determination in triplicate.

    Alternative groups in the class can use TSA or Sabaroud Dextrose Agar.

    Colonies develop on the agar surface during incubation.Count the colonies and express your results as CFU/area/time sampled.

    Ha!(sle y )ilter.(is syste& collects 'articles "ro& t(e air onto a &e&brane "ilter% .(e

    &e&brane "ilter is t(en 'lace# onto an agar &e#iu& to collect .otalbacteria or =easts$&oul#s%

    (at agar oul# you use to collect total bacteria>

    ??????????????????

    (at agar oul# you use to collect yea st s$ &o ul# s>

    ??????????????????

    (at ag ar oul# you use to collect !ta' (ylococci>

    ??????????????????

    !a&'le "or 10 &inutes set ting t(e 'u&' a t 30l$&in%

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    alculate t(e /olu&e o" air sa&'le# in

    & 3???????????????????????

    @;'ress you resul ts a"ter incubat ion as s$& 3 air%

    #'# #$ra%e * 'ir * sa+&l er..(is unit collec ts 'a rticl es car ryi ng &icroorgan is&s by

    i&' action onto t(e sur"ac e o" ag ar &e #iu & in regular

    contac t +A, 'lates %

    .(e ag ar & e# iu & ca n be sel ec te # to reco /e r any gro u' o"

    &icroorganis&s%

    Bn t(is 'ract ical use .!A to reco/er bacteria

    !abarou# e;trose agar to reco/er =east s$&oul#s

    Mannitol !al t to eco/er Presu&'ti/e !ta'(ylococci %

    !a&'le 1000 l o" air%

    Bncuba t e t(e aga r 'la te s at t(e a''ro'ri at e te&'era t u res %

    A"ter incubati on re'ort on t(e nu&ber o" & icroorgan is&s

    reco/e re# 'er & 3 air%

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    Esti +a t i o n o bio b$ rd e n on &ro d$ % t s .Bn or#er to esti&a te t(e e;ten t o" conta &in ation on

    'ro#ucts t(e articl e in *uestion &ust be rinse# in #iluent

    an# t(e nu&bers o" s #e te r&ine# eit(er by 'our ' la te

    &et(o# or &e&bra ne "iltra tion%

    Met(o#%

    Pre'ara t ion o" 'ro#uct "or biobur#en is usually car ri e# out

    in t(e la&inar "lo sa"ety (oo#%

    A sa&'le o" 'ro#uct is &ay be c(o''e# using a sterile scissors an# t(e

    'ieces 'lace# in one litre o" #iluent%

    sually three pieceso" 'ro#uct are assaye# an# t(e result is e;'resse#

    as t(e &ean 'er one ite& o" 'ro#uct%

    .(e #ilue nt is s(a -e n "or 15 &ins to #islo#g e att ac ( e#

    &icroorganis&s%

    A% Pass one ali*uot o" 250 &l o" #iluent t(roug( a

    &e&br an e using a sterile &e &br a n e "iltration

    a''aratus %

    Plac e t( e &e &b r a n e car e"ully gri# si#e u' onto t( e

    sur"ace o" a .!A 'late%

    abel an# incubate aerobically 37 "or 48 (rs%

    @;'ress your resul t as $lit re o" #iluent i%e% 'er a&ount

    o" 'ro#uct in t(e #iluent or 'er in#i/i#ual 'ro#uct %

    B. Pass a second aliquot o" 250 &l o" #iluent t(roug( a

    &e&br an e using a sterile &e &br a n e "iltration

    a''aratus %Plac e t( e &e &b r a n e car e"ully gri# si#e u' onto t( e

    sur"ace o" a .!A 'late%

    ab el an # incu ba t e anaerob i ca l l y in a gas Car 37

    "or 48$72 (rs%

    C. Pass a third aliquot o" 250 &l o" #iluent t(roug( a

    &e&br an e using a sterile &e &br a n e "iltration

    a''aratus %

    Place t(e &e &b ra n e onto t(e sur"ac e o" a !abarou #

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 3" 30

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    e;trose agar 'late %

    abel an# incubate aerob i ca l l y 25 "or 5 #ays%

    A"ter incub atio n coun t all colonie s a'' e ar in g on t( e

    &e &b ra n es an# e;'re ss t(e biobur# en as s 'er'ro#uct%

    it( t(e re&ai ni ng #iluen t car ry out a 'la te coun t using

    t( e sa & e ag ar &e #i a%

    Pre'are a 1:10 #ilution o" t(e #iluent using 9 &l ingers%

    Bn tri'licat e a## 1 &l o" t (e original sa&'l e an# t(e 1:10

    #ilution to t(ree agar 'lates %

    are"ully a## &olten .!A sirl allo to set an# incubate 37D "or 48 (rs%

    Bn tri'licat e a## 1 &l o" t (e original sa&'l e an# t(e 1:10

    #ilution to t(ree agar 'lates %

    are"ully a## &olten .!A sirl allo to set an# incubate

    37D in t(e gas Car "or 48$42 (rs%

    Bn tri'licat e a## 1 &l o" t (e original sa&'l e an# t(e 1:10

    #ilution to t(ree agar 'lates %are"ully a## &ol ten !aborau# e;trose agar sirl a llo

    to set an# incubate 25D "or 5 #ays %

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 31 31

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    Res$lts:'ir 'nalysi s :

    Biotes

    tCFU /m3

    )il ter

    CFU /m3

    #' #

    CFU /m3

    Casell

    aCFU /m3

    'nders

    onCFU /m3

    'nderson

    E non

    res'irab

    le

    E

    res'irab

    le

    Total bacteria

    Yeasts/moulds

    Mannitolfermenters

    TotalMicroorganisms

    #! abs:#ete r&ine t(e sabbe# ar ea %

    C),- / %+ 0

    #$r a% e

    s ! a b b e d

    %olior+ s 1otal ba%t eri a

    Conta% t &l ate s .#ete r&ine t(e contact ar ea %

    C),- %+ 0

    #$r a% e%ont a% t ed

    1otalba%ter ia

    + an ni t ol er+ent e

    rs

    %olior+s

    yea s t s and+o$lds

    Co++ en t on res $l ts :

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 32 32

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    Personal Hygiene%

    C), &er handNa+e beor e !as h ater !as h

    Co++ en t on res $l ts :

    Bio b$ rd e n o n &r od $ % tC),-&rod$%t

    ba%ter ia

    des%ri& t ion o &rod$% t 'erobi% 'naero b i % yea s t s - + o $ld s

    Co++ en t on res $l ts :

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 33 33

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    Mi%ro bi o l o g i % a l 'nal y si s o #oil s an d

    # e d i + e n t s .

    Bn t(ese 'rac ti cal s e ill ana ly se soils an# se# i&en t s "or a / ari ety

    o" &icrob ial 'o'ula t ions in or#er to get so&e i#ea o" t(e #i/ersi ty o"&icr oor ga ni s &s 'r es e nt in t( es e e n/ir on & e n ts % Bt is 'os si bl e to

    "urt( er a na lys e t( es e soils to #isco/ er t( e "unc tio ns t( at t( es e

    &icro bial 'o 'u la t io n s a re r es' o ns ible "or in t( ei r n atu ral ( ab it a t

    i%e % r ecyc ling carbo n ni trog en sul'( u r an# '( os' ( o rus as ell a s

    'ro#uction o" organic aci#s an# gass es an# &obil i< ation o" &et als

    an# &icrob ia l cor ro sion % eg ra# a t io n or # e to ;i "ica tion o" a i# e

    /arie ty o" to;ic org anic c(e &i ca ls inclu#in g (y#r oc ar b on s F

    ali' (a ti c ar o& a t ic a n# ( al og e n a t e # ar e als o car ri e# out by t( es e

    'o 'ula tions%

    !oils are a co& 'l e; an# (et er og e no u s en/iro n& e nt cont ai nin g

    &a ny #iscontin uo us &icro( abit at s an# t(er e"or e 'res en ts a#i""icult c(al lange to t(e in/est igator %

    Bn t(e "irst 'ract ical #eter&ine t(e "olloing:

    Mi%robial Po&$la t i o n Metho d Medi$ +.otal )acterial Gu&bers

    's yc (ro'(iles s'rea # 'late 'e'ton e ye as t

    e;t rac t agar%

    &eso' (iles Pour 'late 'e'ton e yeas t e;trac tagar%

    t(er &o ' (iles Pour 'late 'e'ton e yeas t e;trac t

    agar%

    .otal ungi+=eas ts $Moul#s, Pour 'late Malt Agar+aci#i"ie#,

    Actino&yc e t e s Pour 'late Actino&yc e t e agar

    Method: ar e" ully eig ( out 10 g o" s oil a n# a ## to 90 &l #ilu en t in !id e

    ne%(ed "las-es%

    Mi; b y gen tl e s(a-in g "or 5 &ins% to #is' er se &icroor ga ni s &s

    into sus' en s io n % Allo ( ea/ y ' ar ti cula t es to set tl e ou t% 1hi s is

    th e 23 42 dil$tio n % Go car ry ou t ser ia l # ilu tion in 90 &l # iluen t s to 1 0 6 %

    5 )or the ba%t eria using t(e pour pla t e tec h n i q u e a# # 1 &l o"

    sa&' le in # u'li ca te "ro & 1" $6% 1" $5% 1" $4% 1" $3 to e ight ' e tr i #is( es

    labelle# "or 22 re' ea t "or 32 an # 5 5 % A## coole# &ol ten'e'ton e ye as t e;trac t agar &i; care"ully%

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 34 34

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    (e n co &'l et e ly soli# in/er t a n# incu ba t e seri es at 22 32

    a n# 55 e;a&ine reg ula rly u ntil n o "ur t( e r colo nies a'' ear on

    t( e 'la te s a n# not e t (e nu &b e r s %

    or t(e &sy%hro&hi le s t( e 'o ur 'la te t ec (ni *u e ca nn ot b e us e#

    as t(e te &' e ra t ur e o" t(e ag ar oul# -ill t (e (e at sen siti/ ebacteria% Usin g th e spr e a d pla t e te ch ni q u e 'i'et te 0%1 &l o "

    sus 'e n si on "ro& 1" $5% 1" $4% 1" $3 an# 1" $2 onto t(e prepo&red

    chilled agar an# s'rea# e/en ly it( t(e glass s'rea# er % Allo to

    #ry an# incub a te a t 4 7 "or s e6 e n da ys .

    )or th e $ ng i &sin g th e po &r plat e t ec hn i' & e a## 1 &l o"

    s a& 'l e "ro & e ac ( #ilution 1" $5% 1" $4% 1" $3 an# 1" $2 1" $1 to two

    'etri #is(es% A## coo le# &ol ten Malt Agar +aci #i"ie# 'H 4%5,

    &i; care"ul ly% (en co&'lete ly soli# label in/ert an# incubate

    'airs at 22 until t(e ne;t class%

    )or t h e a %t in o + y % e t e s using t(e po&r plate techni'& e a# # 1

    &l o" s a& 'l e "ro & e ac ( #ilutio n 1" $5% 1" $4% 1" $3 an# 1" $2 1" $1 to

    two 'etri #is(es% A## co ole# &ol ten Actino&yc e t e agar &i;

    care"ul ly% (en co&'lete ly soli# label in/ert an# incubate 'ai rs

    a t 2 2 until t(e ne;t class%

    e'or t t(e nu &b er s o" Is ' er g dry wei g h t of soil.

    eter&in e t(e dr y ! t . o th e s oi l u sing 10g o" et soil in &eta l

    tr ays in t( e o/ en a t 1 04 "or 2 4 (r s% an# #ry to co ns tan t eig( t

    using a #esiccator %

    Mea su re t( e 'H o" t (e soil a n# recor #% Ma-e a slurr y o" t (e soil

    +10 g, in al 2solution +20 &l 0%01M al2,%

    Media

    Jlycerol aesin agar: in 1000&l #eion ise# ater #issol/e t(e

    "olloing: 10 g glycerolF 0%3 g caesinF 2%0 g KG3F 2%0 g GalF2%0g K 2HP 4F 0%05g Mg! 4%7H 2F 0%02 g a 3F 0%01 g

    e! 4%7H2F 18 g agar an# 50 &g cyclo(e;i&i#e% A"ter

    autocla/ing a#Cust to 'H 7%0 it( conc% Hl%

    Malt e;tract agar + Aci#i"y to 'H 4%5 it( tar tar ic aci#,

    Pe'to n e yeas t e;t rac t agar : in 10 00 &l # eioni se# a ter #is sol/e t(e

    "olloing : 5 g 'e' tone 3 g yeas t e;t rac t an# 15 g agar % A"ter

    au tocla/ ing but (en coo l a## 10 &l 1%0M al 2% A"ter

    autocla/ing a#Cust to 'H 7%0 it( conc% Hl

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 35 35

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    Res$lts

    C),- g dry ! e i ght soi l

    Ba%teria

    #oil ty&e 'syc(ro'(ile

    s

    &es o' (iles t(er &o '(ile

    s

    '%tino+y%

    etes

    Ye

    ld s

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 36 36

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    Isolation of Starch Protein and DNA degraders.

    In order to demonstrate the presence of degraders form soil you can

    transter colonies from the mesophile plates from the previous

    experiment onto agar containing starch, protein and DNA.

    Microorganisms that live in soil habitats frequently encounter substratesin the form of polymers, and in order to extract nutrients for growth

    must degrade the polymers to soluble components e.g. in the case of

    carbohydrates, i.e. starch is hydrolysed by the enzymeamylaseto

    produce sugars.

    What are the components that make up proteins and Nucleic acids?

    Materials:

    Each person needs one plate of:- starch agar; Casein agar and DNase

    agar.Procedure:

    Using a loop aseptically transfer a portion of a colony from the agar

    plate from the last practical onto the agar medium under test.

    You can transfer eight-ten suspect colonies if you carefully spot the

    colonies onto the plates with sufficient space between colonies. Incubate

    at 22C for 48 hrs.

    Include uninoculated plates as controls.

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 37

    .!A agar it(

    eit( er s ta rc(

    !ource o"

    colonies "ro&

    1

    2

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    After incubation, examine the plates as follows:-

    For starch degraders, flood the plate with Iodine solution and and leave

    for a few minutes to allow the starch to react with the iodine. Starch

    degradation is revealed by clear zones surrounding the degrading

    colonies.For protein degraders, a clear zone around any colony indicates protein

    degradation.

    For DNA degraders, flood the plate with 1M HCl and leave to develop.

    HCl precipitates DNA in the agar leaving clear zones surrounding

    colonies with the ability to degrade DNA.

    Report your results.

    What proportion of the colonies degrade the polymes, and do the same

    colonies degrade all the polymers?Record your observations.

    If time permits carry out a Gram stain on the colonies.

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 3 38

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    ESTIMATION OF MICROBIAL ACTIVITY BY FLUORSCEIN

    DIACATATE HYDROLYSIS

    Spectrophotometric determination of the hydrolysis of fluorescein

    diacetate (FDA) to fluorscein can be used as a sensitive and rapidmethod for determining microbial activity in soil. FDA is hydrolyzed by

    a variety of enzymes i.e. proteases, lipases and esterses to fluorscein and

    changes in fluorscein can be followed by measuring the absorbance at

    490nm.

    METHOD.

    FDA is dissolved in acetone 2mg/ml and stored as a stock solution (at-20C).

    Replicate samples of soil (10g) are placed in conical flasks with 20ml

    sterile sodium phosphate buffer 60mM, (pH 7.6).

    To each sample,0.1 ml FDA is added (10 g/ml final concentration).

    The flasks are incubated on the shaker at 27C for 1-2 hr.

    The reaction is terminated by adding acetone (50% final conc.).

    The samples are then centrifuged for 5 mins. followed by filtration to

    clear the sample.Absorbance is then determined by reading at 490nm using a

    colourimeter.

    Autoclaved soil treated exactly the same way is used as a control blank.

    Activity is expressed as Abs@ 490/hr/g dry wt soil.

    Samples:

    Loam soil sieved, loam soil with various additives i.e. diesel, starch,

    cellulose, protein.

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 3! 39

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    I#OL'1ION O) B'C1ERIOPH'GE.

    PRELIMIN'RY ENRICHMEN1 O) 7PH'GE.

    a seage or ri/er ater is centri"uge# an# t(e su'ernatant collecte#% .(e

    bacteria are re&o/e# "ro& t(e su'ernatan t eit(er by +e+brane iltration or

    by ina%ti6ation $sing %hloroor+ +si; or se/en #ro's o" c(loro"or& are a##e#

    to 10 &l o" sa&'le% .(e tube is s(a-en to ensure t(at t(e ater is saturate#

    it( t(e sol/ent% .(e c(loro"or& is alloe# to settle%

    Bn ater sa&'les (ere t(e concentrations o" /iruses is lo it &ay be

    necessary to concentrate t(e /iruses by a#sorbing t(e& onto a &aterial suc(

    as (y#ro;ya'atite or alu&iniu& sul'(ate%

    2. A## t(e "iltere# sa&'le containing t(e /irus to about 20 g o"

    (y#ro;ya'atite in a 1 l conical "las- an# s(a-e ra'i#ly "or 5 &ins% ollect t(e

    (y#ro;ya'atite in a )uc(ner "unnnel an# #iscar# t(e "iltrate% .(e /iruses on

    t(e (y#ro;ya'atite can be elute# using a #ilute '(os'(ate bu""er +0%8M

    Ga 2HP 422%6g$100&l +80&l, L 0%8M GaH 2P424%96g$200 &l +20&l,,%

    0. Gaturally occurring coli'(ages can be concentrate# accor#ing to t(e"olloing 'roce#ure:

    2 &l o" a 10E Al2+!4,3 solution is a##e# to 1 litre o" t(e sa&'le t(e 'H is

    a#Custe# to 5%5 it( Hl an# t(e sa&'le le"t o/renig(t at 6% .(e Al+H, 3

    "locs (ic( (a/e "or&e# toget(er it( t(e a#sorbe# '(ages are centri"uge# at

    3000 g "or 5 &in%

    .(e se#i&ent is t(en resus'en#e# in 10 &l 0%1 M citrate bu""er it( a 'H o"

    4%7%

    1 &l concentrate is &i;e# it( 0%5 &l o" an E.colisus'ension containing 108$ &l an# it( 5%0 &l so"t agar% .(e tube containing t(e &i;ture is

    t(oroug(ly &i;e# an# 'oure# into a Petri #is( containing 20 &l try'tone

    soya yeast e;tract agar% .(e 'lates are counte# a"ter 24 (ours incubation at

    37%

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 4" 40

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    )rain Heart Bn"usion brot( +#ouble strengt(, +50 &l ! in 200 &l conical

    "las-s, is 're'are# an# sterilise#%

    .o t(is 50 &l o" t(e ater sa&'le sus'ecte# o" containing bacterio'(age is

    a##e#%

    A"ter &i;ing ell 20 &l o" a young culture o"E.coli +68 (rs ol#, in 'e'tone

    ater is a##e# an# incubate# on t(e s(a-er table "or 810 (rs or until a

    #ecrease in turbi#ity is obser/e#%

    Pre'are a control to obser/e t(e grot( o"E.coli un#er t(e sa&e con#itions%

    .(e analysis is carrie# out in #u' licate%

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 41 41

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    I#OL'1ION 'N8 EN,MER'1ION O) 7PH'GE.

    A"ter incubation t(e bacteria are re&o/e# "ro& a s&all /olu&e o" brot( by

    centri"ugation an# &e&brane "iltration%

    .(e nu&bers o" bacterio'(age in t(e enric(e# brot( are #eter&ine# by

    're'ar ing a series o" #eci&al #ilutions in 1$4 str% ingerIs solution%

    Alternativel(% i# onl( thepresence or absenceo# the )acteriophage is re'&ired to )e

    demonstrated% then a more rapid proced&re can )e carried o&t.

    *ive ml o# the enriched )roth are trans#erred to a test t&)e and placed in a +ater )ath

    at 56,- #or 3"min. his is s#icient treatment to eliminate the )acteria +hile

    /eeping the )acteriophages active. he presence o# the vir&ses can )e detected )(

    #ollo+ing the proced&re )elo+.

    .(e nu&bers o" I'(age in t(e #ilutions can enu&erate# eit(er by a Miles 9

    Misra s$ra%e dro& tec(ni*ue to inoculate lan cultures o"E.coli or by a &o$r

    &late te%hni$e.

    an cultures o"E.coli can be 're'are# by s'rea#ing 0%1&l o" a 24 (r% cultureo"E.coli onto t(e sur"ace o" a ell #rie# agar 'late% Allo t(e 'lates to #ry%

    .(e I'(age sus'ension is t(en #ro''e# "ro& calibrate# #ro''ers onto t(e

    sur"ace o" t(e 'late an# incubate# o/ernig(t at 37%

    A"ter incubation t(e 'resence o" I'(age is s(on by a clear area or se/eral

    s&all clear areas -non as PL';,E# (ere t(e lan o" bacteria (as been

    lyse# by t(e I'(age%

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 42 42

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    'lternati6e +ethod.

    .(e &o$r &late te%hni$e is carrie# out by inoculating 3 &l .!A +-e't &olten

    at 50, it( 1 &l or 0%5 &l o" an o/ernig(t brot( culture o" t(e (ost

    bacteriu& &i; ell to #istribute t(e cells e/enly in t(e agar% .o t(is is a##e#

    0%5 &l $0%2 &l o" t(e bacterio'(age #ilution again &i; ell%

    Work quickly to prevent the agar from solidifying, preferably in a warm

    environment.

    Pour t(e &olten agar onto t(e sur"ace o" a +armed .!A 'late an# incubate at 37

    o/ernig(t% lear areas or 'la*ues (ere t(e bacteriu& (as been lyse# by t(e

    I'(age are counte#%

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 43 43

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    Enri% h+ e n t Isol at io n O 8e gr a d e r s O

    Organi% Conta+ina nt s

    Bn t(is series o" 'ractic als you are re*uire # to

    isolate an# 're'are a 'ure culture o"

    &icroor ga ni s& ca' abl e o" grot ( on one o" t(e

    organic c(e&icals liste# belo%

    .(e 'roc e# u re "or isolatio n is on e o" enric( & e n t

    isolation in batc ( cultur e alt(o ug ( so& eti &e s

    contin uo us cultur e tec (ni *u e s are us e# to isolat e

    organis &s it( a lo a""inity to t(e organicconta&inant in *uestion%

    .(e sourc e o" t(e org anis & s "or t(is 'ra ctic al is

    acti/ at e # se ag e alt(o ug ( soil re 'r es e n t s a /as t

    reser/oir "or all -in#s o" &icroorganis &s%

    Proce#ure:

    1% .o t(e 50 &l acti/ate# seag e in a 250 &lconical "las- a## t(e c(e&ical un#er

    in/e stig a tio n as t(e sole car bo n sour ce +200

    &l$l,%

    2% Bncub at e on an orbital s(a- er at 25 "or se/en

    #ays%

    3% A"ter incuba ti on str ea- a sa& 'le onto .!A #orsingle colon( isolation an# incubat e "or 4 7

    #ays at 22 25% @;a&ine #aily "or grot(%

    4% Many colonies &ay #e/elo' on t(e agar

    &e#iu& an# all &ay be trea te# as sus'ect

    colonies ca' abl e o" #egr a#in g t(e c(e &ic al

    un#er in/est iga t ion as t(ei r sole carbon source %

    5% !elect a single colon( "or in/est iga t ion #escribe

    Dr. Michael A. Broa ders De pt . Environ m e n t al Sc ience. Sli go 44 44

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    t( e colony &or '( olo gy an # tra ns" er a 'ortio n

    into &ineral salts &e#iu& containing t(e

    c(e&ical un#er in/estiga tion as t(e sol e

    car bo n sour ce .

    6% Bncu ba t e on t(e s( a- er tabl e e; a&i ne #aily an #

    note turbi#i ty as e/i#ence o" grot( %

    7% !trea- aga in on to .!A #or single colon( isolation

    an# incub at e "or 4 7 #ay s at 22 25% Again

    e;a&ine #aily "or grot(%

    8% e' ea t ste 's 56 an# 7 until you are con"i#e ntt(at t(e cultur e gros in t(e &in er al &e #iu &

    using t(e selecte # c(e&ical as sole carb o n

    source %

    9% @;a&in e t(e cell &or '( olo gy an# re'or t Jra &

    stain s(a'e an# si

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    (ec- t(e M!! s(eets "or sa"e ty #ata to;ici ty le/els an# any

    ot(er rel e/ an t # ata %

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    THE NITROGEN CYCLE.

    Transformations of Nitrogen compounds are carried out by a variety of

    microorganisms. Many of these microorganisms occur in soils as well as

    in aquatic and marine habitats. In this series of practicals you will

    demonstrate the involvement of microorganisms in various phases of thenitrogen cycle.

    1. Ammonification.

    Ammonification is the hydrolytic decomposition of complex

    nitrogenous substances to yield ammonia (NH3), and various other end

    products. A wide variety of microorganisms (bacteria and fungi) are

    capable of breaking down the proteins of animal and vegetable matter.The ammonia thus liberated is then available as a nutrient and also to

    nitrifying microorganisms.

    Materials. Test tubes containing 4% peptone solution.

    Soil, manure, sewage, cultures ofBacillus cereus, Pseudomonas

    fluorescens andProteus vulgaris, spotting tile, Nesslers reagent and pH

    paper.

    Procedure. Inoculate tubes of peptone with each of the above and

    incubate at 27C. Remember to leave one tube as an uninoculated

    control. Test for the presence of NH3with Nesslers reagent on a spotting

    tile.

    Note the pH, record the results.

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    2. NITRIFICATION.The transformaton of NH3to N0-3in soils is carried out by highly

    specialized aerobic, autotrophic bacteria.Nitrosomonas derives itsenergy for growth by the oxidation of NH3to N0-2, andNitrobacter

    completes theoxidation of N0-2to N0-3. The energy yield from these

    oxidations is very low and consequently the bacteria grow slowely and

    their isolation takes a long time under laboratory conditions.

    However, it is possible to demonstrate the oxidation of NH3to N0-3by

    using enrichment shaker flask culture.

    MATERIALS. 2 x 250ml conical flasks containing 100 ml of the

    enrichment medium as detailed below.

    NITRITE FORMATION MEDIUM NITRATE FORMATION

    MEDIUM

    (NH4)2SO4.................. .1.0g

    NaNO2............................0.5gK2HPO4..........................1.0g

    K2HPO4. 7H2O...............1.0g

    MgSO4.7H2O..................0.5g

    MgSO4. 7H2O................0.3g

    FeSO4.7H2O..................0.04g

    FeSO4. 7H2O................0.04g

    CaCO3...............................10g

    Na2CO3........................1.0g

    NaCl..................................2.0g

    NaCl..............................0.5g

    H2O........................................1L

    H2O....................................1L

    pH..........................6.8-7 pH.........................6.8-7

    Autoclave the flasks at 15 psig/15 mins.

    Spotting tiles, pH paper and the following reagents; Nesslers,

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    Sulphanilic acid, naphthalamine, diphenylamine in conc. H2S04, urea

    powder, dil. H2S04and test tubes.

    PROCEDURE.

    To each flask add 9.0 g of test soil. Incubate the flasks on the shakertable at 220 r.p.m. and at 27C.

    Each flask should be tested for the presence of NH3, N0-2and N0-3using

    the spotting tiles and the procedure as detailed below.

    Present the results in a table, showing the appearance of N0 2and N03during the test period.

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    3. DENITRIFICATION. (dissimilatory nitrate reduction).

    Under anaerobic conditions many bacteria can use the oxygen in nitrites

    or nitrates to oxidise reduced organic matter. Nitrate is used as the

    terminal electron acceptor and is reduced eventually to nitrous oxide.Microbial denitrification leads to a loss of inorganic nitrogen

    MATERIALS Test tubes containing denitrification medium as detailed

    below, soil sample, Pseudomonas fluorescence, spotting tiles, reagents

    for nitrogen analysis.

    Denitrification medium. NaN03,1g; Na citrate, 9.5g; K2HP04, 2.0g;CaCl2, 0.2g; FeCl3,trace;

    H20 to 1 L. Check the pH, dispense into test tubes and autoclave at 15

    psig for 15 minutes.

    PROCEDURE :

    Inoculate four tubes of denitrification medium with the soil samples andthe culture of Pseudomonas. and incubate at 27C. Remember to retain

    one tube as an uninoculated control. Test for the presence of nitrate and

    nitrite during the incubation period. Tabulate your results.

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    Qualatative tests for ammonia. nitrite and nitrate.

    Test for Ammonia.

    Put a drop of culture solution onto a spotting tile. Add one drop ofNessler's Reagent. A deep yellow to brown colour indicates positive for

    Ammonia.

    Test for Nitrite. Add one drop of Sulphanilic acid and one drop of

    Naphthalamine to a drop of culture solution. A red colour indicates

    positive for Nitrite.

    Test for Nitrate.

    Add one drop of Diphenylamine (in conc. H2S04) to a drop of the

    culture solution. A blue colour inddicates positive for Nitrate. However,

    Nitrite will also give a blue colour in this test, therefore to confirm the

    presence of Nitrate it is necessary to destroy any Nitrite that might bepresent by boiling a little of the culture solution with urea plus dil.H2S04in a test tube. Cool and repeat the test for Nitrate.

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    4. NITROGEN FIXATION.

    Microbial nitrogen fixation results in a net input of nitrogen into the

    system and is carried out by a variety of symbiotic and free living

    nitrogen fixing microbes that live in the soil.Azotobacter isa highlyaerobic, free living nitrogen fixing bacterium found in soil. Azotobacter

    can be isolated from soil by sprinkling a little onto the surface of an agar

    medium or into a liquid enrichment medium lacking nitrogen, as shown

    below.

    N-FREE MANNITOL/SUCROSE AGAR.

    For isolation and cultivation ofAzotobacter from soil.

    Mannitol............................................................. ..10 g

    or

    Sucrose............................................................... ..1 0 g

    K2HP04.............................................................. ...0.5 g

    CaC03................................................................ ...0.5g

    MgS04.7.H2O..................................................... ...0.025g

    FeS047.H2O........................................................ ...0.025gNa2MoO4........................................................... ....0.0025g

    Agar................................................................... ....1.2/1.5g

    Water.................................................................. ....1 L

    pH..................................................7.2-7.4

    MATERIALS. Plates of nitrogen free agar medium, soil samples and

    Ringers diluent.

    PROCEDURE. Sprinkle fine soil particles sparsly over the surface of

    the agar plates. Incubate the agar plates at 27C until the next practical

    period and look for typicalAzotobacter colonies. These should appear as

    raised, moist, glistening white colonies. Examine the cell morphology

    by Gram staining.

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    Attempt to purify the cells by suspending a portion of a well isolated

    colony in Ringers and restreaking onto the same medium.

    Alternatively, N-free liquid medium can be prepared andAzotobacter

    isolated and purified by repeated subculture in shake flask culture.

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    ENUMERATION, ISOLATION AND CHARACTERISATION OF

    MICROORGANISMS FROM SOIL.

    Before begining the microbiological analysis, determine the moisture

    content of the soils so that you can express the microbial count as CFUper gramme dry weight of the soil. In the preliminary investigation you

    will estimate the numbers of bacteria, fungi and actinomycetes in the

    soil samples.

    MATERIALS. Soil samples, 90ml diluents, sterile 10 ml and 1 ml

    pipettes.

    Culture media; Soil extract agar for total bacteria,Dextrose Nitrate agar for actinomycetes,

    acid PDA and Rose Bengal agar for fungi,

    McConkey or Violet Red Bile Agar for coliforms.

    SOIL EXTRACT AGAR.

    K2HP04..............................0.5g Soil Extract

    Dextrose............................ 0.1g Mix 1kg soil with 1.51 H20,

    Soil Extract.......................... 11 autoclave at 15 psig/30 mins.

    Agar............................. 12/1 5g Filter.

    pH.................................6.8-7.0

    Sterilize at 15 psig/15 mins.

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    Medium for the isolation of Actinomycetes.

    DEXTROSE NITRATE ACTIDIONE AGAR.

    Agar---------------------- l5 gDextrose------------------l gKH2PO4----------------------0.1 g

    NaN03--------------------0.1 g

    KCl -----------------------O.l gMgS04.7H20-------------O.l g

    H2O-----------------------l l

    pH-------------------------7.0

    Autoclave 15 lbs / 15 mins.

    Acid PDA.

    To Potato Dextrose Agar add sufficient sterile H2S04to bring the pH

    to pH 4.0. Add the acid while the agar is still molten but cool and after

    autoclaving.

    Rose Bengal Antibiotic Agar.

    Glucose 10 g

    NH4NO3 1.0 g

    Yeast extract 2.0 g

    MgSO4.7H2O 0.2 g

    KH2PO4 3.0 g

    FeSO4.7H2O 0.0025 g

    Water 1 literAgar 15 g

    Rose Bengal Dye 0.09 g

    Neomycin 0.1 g

    Neomycin is best filter sterilized and 1 mg added to the dry Petri dish before

    adding the molten agar.

    PROCEDURE. Add 10 g soil to 90ml of diluent and shake vigerously

    for 10 mins to suspend the soil completely. Allow the large particulates

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    to settle and continue decimal dilution to 10-7.

    Prepare pour plates in duplicate using 1 ml samples of appropiate

    dilutions into the selected agar media. Incubate at 25C and examine the

    plates periodically for development of the colonies. Tabulate your

    results.

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    @nric( &e nt Bsolation o" #egra # es o" organics

    suitable "or )iore&e #ia tion%

    Bn t(is series o" 'ractic als you are re*uire # to

    isolate an# 're'are a 'ure culture o"

    &icroor ga ni s& ca' abl e o" grot ( on one o" t(e

    organic c(e&icals liste# belo%

    .(e 'roc e# u re "or isolatio n is on e o" enric( & e n t

    isolation in batc ( cultur e alt(o ug ( so& eti &e s

    contin uo us cultur e tec (ni *u e s are us e# to isolat e

    organis &s it( a lo a""inity to t(e organic

    conta&inant in *uestion%

    .(e sourc e o" t(e org anis & s "or t(is 'ra ctic al is

    acti/ at e # se ag e alt(o ug ( soil re 'r es e n t s a /as t

    reser/oir "or all -in#s o" &icroorganis &s%

    Proce#ure:

    1% .o t(e 50 &l acti/ate# seag e in a 250 &l

    conical "las- a## t(e c(e&ical un#er

    in/e stig a tio n as t(e sole car bo n sour ce +200

    &l$l,%

    2% Bncub at e on an orbital s(a- er at 25 "or se/en

    #ays%

    3% A"ter incuba ti on str ea- a sa& 'le onto .!A #orsingle colon( isolation an# incubat e "or 4 7

    #ays at 22 25% @;a&ine #aily "or grot(%

    4% Many colonies &ay #e/elo' on t(e agar

    &e#iu& an# all &ay be trea te# as sus'ect

    colonies ca' abl e o" #egr a#in g t(e c(e &ic al

    un#er in/est iga t ion as t(ei r sole carbon source %

    5% !elect a single colon( "or in/est iga t ion #escribe

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    t( e colony &or '( olo gy an # tra ns" er a 'ortio n

    into &ineral salts &e#iu& containing t(e

    c(e&ical un#er in/estiga tion as t(e sol e

    car bo n sour ce .

    6% Bncu ba t e on t(e s( a- er tabl e e; a&i ne #aily an #

    note turbi#i ty as e/i#ence o" grot( %

    7% !trea- aga in on to .!A #or single colon( isolation

    an# incub at e "or 4 7 #ay s at 22 25% Again

    e;a&ine #aily "or grot(%

    8% e' ea t ste 's 56 an# 7 until you are con"i#e ntt(at t(e cultur e gros in t(e &in er al &e #iu &

    using t(e selecte # c(e&ical as sole carb o n

    source %

    9% @;a&in e t(e cell &or '( olo gy an# re'or t Jra &

    stain s(a'e an# si

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    (ec- t(e M!! s(eets "or sa"e ty #ata to;ici ty le/els an# any

    ot(er rel e/ an t # ata %

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    Ecology of Phototrophs: Preperation of Microcosm to examine

    Microbial ecology, The Winogradsky Column.

    To 20-25 g of surface sediment from a fresh water pond add 0.5 g

    CaSO4, and some organic matter, in the form of shredded filterpaper/ caesin.

    Put the mixture into a 500 ml measuring cylinder and fill with fresh

    water.

    Expose the column to natural daylight at room temperature.