Environmental Microbiology Athens September 2010...

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http:// http:// www.bio.warwick.ac.uk www.bio.warwick.ac.uk /wellington /wellington Environmental Microbiology Environmental Microbiology Athens September 2010 MSc Athens September 2010 MSc Microbial detection methods Microbial detection methods E M H Wellington, Department of Biological E M H Wellington, Department of Biological Sciences, Sciences, University of Warwick, Coventry UK University of Warwick, Coventry UK

Transcript of Environmental Microbiology Athens September 2010...

http://http://www.bio.warwick.ac.ukwww.bio.warwick.ac.uk/wellington/wellington

Environmental MicrobiologyEnvironmental Microbiology

Athens September 2010 MScAthens September 2010 MSc

Microbial detection methodsMicrobial detection methods

E M H Wellington, Department of Biological E M H Wellington, Department of Biological Sciences, Sciences,

University of Warwick, Coventry UKUniversity of Warwick, Coventry UK

Objectives for enumeration and isolation of bacteriaObjectives for enumeration and isolation of bacteria

Detection of pathogen reservoirs Detection of pathogen reservoirs

Determination pollution impactsDetermination pollution impacts

Exploiting bacterial diversityExploiting bacterial diversity

Investigate aspects of biogeochemistryInvestigate aspects of biogeochemistry

Tracking Tracking biocontrolbiocontrol inoculants / inoculants / GMOsGMOs

Approaches to isolating bacteria from the environmentApproaches to isolating bacteria from the environment

* Pretreatment of the sample, enrichments, soil fractionation

* Selective media, baiting, liquid culture, chemostats

* Immunomagnetic capture, lectins, extraction of cells

* Inhibition of dominant groups/fast growing bacteria by use of selective inhibitors such as specific phage, antibiotics, protozoa

Pathogen reservoirs

Case study 1: Detection of enteric bacteria. Monitoring salmonellae in the environment in soil and water

Case study 2: Detection of Mycobacterium species in soil, faeces, potable waters/ animal drinking toughs

Exploiting bacterial diversity

Case study 3: New approaches to detection of novel Pharmaceuticals and enzymes

Extraction and cultivationExtraction and cultivation : : sensitivity sensitivity and selectivityand selectivity

Part 1

Pathogen reservoirs

Case study 1: Detection of enteric bacteria. Monitoring salmonellae in the environment in soil and water

Case study 2: Detection of Mycobacterium species in soil, faeces, potable waters/ animal drinking toughs

Exploiting bacterial diversity

Case study 3: New approaches to detection of novel Pharmaceuticals and enzymes

Application of sewage sludge to land: what is the fate of enteric bacteria in soil?

Sewage treatment and disposal

Fate of exotic bacteria in the environment

Problems to be addressed

lDo exotic bacteria enter a non-culturable state; if so what is physiological state of cells? Extent survival of culturable populationWhich environmental factors induce this state, and what is the mechanism of induction?

lHow can cells be selectively detected and resuscitated?

lCan existing clinical detection methods be appliedSelective isolation media, typing methods, specific antibodies

Growth 0.5h 6h 100h

Changes in Vibrio during multiple nutrient starvation

After Östling et al., 1992

Bacterium

Aeromonas Salmonicida

Agrobacterium tumefaciens

Campylobacter jejuni

Enterobacter aerogenes

Klebsiella pneumoniae

Salmonella enteritidis

Shigella dysenteriae

Vibrio cholerae

V. vulnificus

Reference

Morgan et al. (1993)

Byrd et al. (1991)

Medema et al. (1992)

Byrd et al. (1991)

Byrd et al. (1991)

Roszak et al. (1984)

Islam et al. (1993)

Wolf and Oliver (1992)

Wolf and Oliver (1992)

Examples of the nonculturable state detected in bacteria

Strategies for survival in soil

Stress:

Starvation

Oxidative

Matric potential

Temperature

Pollutants

Resting cells

Spores

Dormant cells'VBNC'

Active state

Germination

Resuscitation

Avoidance by adsorptionto clay / position withinaggregates

Stimulus

Detection of the nonculturable state in soil

Bacterium

Salmonella typhimuriumVibrio harveyiE. coli

Indigenous

Alcaligenes eutrophusEnterobacter clloacaePseudomonas fluorescensPseudomonas aeruginosa

Pseudomonas fluorescensPseudomonas syringaePseudomonas fluorescensFlavobacterium

Method

Direct countluminescence+ yeast extract

CTC stainingmicrocoloniesDirect viable counts (DVC)

Microcolony epifluorescence (AO)DNA / resuscitation

CTC staining

ImmunofluarescenceDVC, CTC staining

Reference

Turpin et al. 1993Duncan et al. 1994

Winding et al. 1994Pedersen & Jacobsen 1993Binnerup et al. 1993Leung et al. 1995Oliver et al. 1995Van Overvbeaket al. 1995Heijnen et al 1995

Viability / activity assays

ReferenceZimmermann et al. 1978

Kogure et al., 1979

Rodriguez et al., 1992

Kaprelyants & Kell 1992

Diaper & Edwards 1994

Nielsen et al., 1999Radajewski et al., 2000Wellington et al., 2003

MethodINT cell respiration

Direct viable count

CTC cell respiration

Rhodamine 123 membranepotentialChemChrom B, flow cytometryFACSMARFISHSIPReview of methods linking structureand function

100

10

1

0.1

0.0120 40 60 80 100 120 140

Times (s)

Survival (%)

Starved 5dViable

DAPI

Log phaseViable

DAPI

Resistance of Vibrio cells to sonication

after Weichart and Kjellberg, 1996

MetMethods must fit objectives:Monitoring only: +/- detection, can be enrichment in situDetection and enumeration: specific, quantitative molecular or

indirect cultivationQuantification and typing: tracking source, establish infectivity-

limited to recovery of cells

Spread of plasmids carrying transposons mediated streptothricin resistance among various bacterial populations (Witte, 1996)

Origin 1982 1983 1984 1985 1986 1987

GI flora of nat- fed pigs - + + + + +GI flora of pig farm personnel - - + + + +GI flora of family of personnel - - + + + +GI flora of healthy adults - - - + + +GU tract infections - - - + + +Shigella sonnei - - - - - +

Meat productsHuman GI tract

Faeces

Slurry Water

Animal feed

Food

Infection

Possible pathways of dissemination of antibiotic-resistant bacteria between animalsand humans

e.g

Genus Selective medium for viable counts

Pseudomonas Pseudomonas CFC agarKings A agar

Salmonella XLD (xylose deoxycholate) agarSalmonella Shigella AgarBrilliant Green agar

Micromonospora Colloidal chitin agarStarch-Casein agar

Streptomyces RASS agar

E.coli McConkey agarEMB agarTryptone Bile agar

Methods for selective isolation of bacteria

Application of sewage sludge to land: what is the fate of enteric bacteria in soil?

l Do salmonellae survive and what affects death rate?

l Can enteric pathogens grow in soil?

l Is there evidence for intracellular growth of pathogenic bacteria within protozoans?

l What are the best strategies for detection and monitoring?

. . . .. .. .. ... ...

The monitoring methods

Directcount(FITC)

ViableCount

Lux phage DNA(PCR)

0 10 20 30 40 50 60 703

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0

0.5

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1.5

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2.5

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3.5

Time (days)

Log cfu/g orlog cells/g soil

Abs.492nm

8

Uncultured populationSalmonella typhimurium

produced in nonsterile soil

Plate count on XLD agar

Fluorescent antibody direct count with live inoculum

UV-killed inoculum

♦ ELISA

15% moisture, 22°C

``

Concentration of cells from soil & DNA extraction

lSample dispersion and cell concentration by differential centrifugation (optional: immuno-magnetic capture (IMC) of cells)

lDNA extraction and purification by either:1) physical disruption of cells, partition & ion-exchange chromatography, or 2) heat-lysis of magnetically captured cells

lMultiplex PCR of triple targets on chromosomeQuantitative PCR (QPCR); MPN or densitometry ofproduct

EXTRACTION OF CELLS FROM SOIL

Breaking forces binding cells to aggregates and clay particles:

Ion exchange-resin based extraction :

Soil + Chelex 100 + PEG 6000 + sodium deoxycholateshake

Differential centrifugation & filtering

Concentrated biomass, separated from soil

Concentration of cells from soil for DNA and other extractions

10 g soil + 10 g Chelex 100 (BioRad) + 10 ml 2.5% polyethylene glycol 6000shake gently for 2 hrs

centrifuge at 177 x g 30 sec

re-centrifuge liquid phase at 3500 x g 15 minthree alternative analyses

DNA extraction viable count immunomagneticresuspend pellet in 1 ml plate dilutions of capture20 mg.ml-1 lysozyme extract on agar resuspend pellet in37ºC for 30 min phosphate buffered saline

(pH 7.2)SDS lysis or physicallydisrupt cells rotate 30min

add magnetic beads coatedprecipitate salt with potassium with antibody (Dynal)acetate

capture bead-cell complex byethanol precipitation of DNA holding magnet against tube

PCR wash and process as required(PCR, selective plating etc.)

Multiplex PCR of putative Salmonella isolates from field samples

Lanes 1-8, putative Salmonella isolates. Lane 9, S. typhimuriumLT2

phoPHinH-li

1 2 3 4 5 6 7 8 9

DNA extracted from soil & PCR of Salmonella -specific targets

Nonsterile soil inoculated with S. typhimurium.

Top lanes =soil DNA (inoculum cfu/g): 1, 10 ; 2, 10 ;

3, 10 ; 4, 10 ; 5, 10 ; 6, negative soil control

Bottom lanes =PCR of H-li from soil DNA.

Lanes 1 - 6 as top lanes; 7, positive control;

8, negative control

7 6

5 4 3

H-li

1 2 3 4 5 6

1 2 3 4 5 6 7 8

0 15 30 454.5

5

5.5

6

6.5

7

7.5

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Time (days)

log cfu/g dry soil viable count

total count

QPCR

QPCR(+lysozyme)

Detection of nonculturable Salmonella typhimuriumcells surviving in nonsterile soil (90% MHC)

Detection of Salmonella typhimurium cells in soil: proportion of active cells

CTC - active count FITC - total count

Factors affecting the survival of salmonella in soil

Factor Comments

Moisturecontent

Bacteria susceptible to desiccation. Survival is longer in wet soils and during rainy periods

Organic matter

Bacterial survival increased when more organic matteris present

pH UK soils range pH 4 to 8. Highest survival pH 7; shorter survival in acid soils (pH 3-5)

Temperature Longer survival at moderate temperatures (>0ºC)

Physical state Physical state of cell when exposed to environment

Sunlight Lower survival a t soil surface by UV action/ photoinactivation /desiccation

Application of sewage sludge to land: what is the fate of enteric bacteria in soil?

l Do salmonellae survive beyond ‘no grazing period’ ? Methods for detection

l Can enteric pathogens grow in soil?

l Is there evidence for intracellular growth of pathogenic bacteria within protozoans?

Soil food web: Soil food web: bacteria consumed by amoebaebacteria consumed by amoebae

•Protozoa are the primary bacterial consumers in soil

•Legionella pneumophila replicates within Acanthamoebpolyphaga

•Enhanced virulence has been noted in L. pneumophilaafter intracellular growth

•Bacteria such as Mycobacterium avium, Listeriamonocytogenes, Chlamydia pneumonia, Escherichia coli, Burkholderia cepacia and Pseudomonas aeruginosa have been reported to survive or replicate within protozoa such as Acanthamoeba

•Investigate S. typhimurium phagocytosed by A. polyphaga doesintracellular survival or replication occur?

•Assess the dynamics of the system, using standardised image sets and time lapse image sequences to determine amoebal grazing rates, duration of digestive cycle, locomotory rate, locomotory behaviour, bacterial growth rates, bacterial survival

Monitoring the interaction

•fis:gfp reporter, fis (factor-for-inversion stimulation protein) is a DNA architectural protein which is involved in specialised DNA recombination events and regulation of gene expression. Fis protein and mRNA levels rapidly increase during early logarithmic growthphase in response to a nutritional upshift but become virtually undetectable during late logarithmic and stationary phases.

•Plasmid pPDT105 was derived from pPDT100 by insertion of egfpdownstream of the fis fragment.

Investigate S. typhimurium phagocytosed by A. polyphaga does

intracellular survival or replication occur?

a) phase contrast image of A. polyphaga with contractile vacuole infected by S. typhimurium.

b) fluorescence image of (a), fluorescence intensity indicates expression of fis.

ba b

Amoebae may facilitate growth of certain bacteria- cocultures non-nutrient agar biofilm , drop inoculate amoebae centre of lawn

c) 3D profile of pixel intensity of (b)

d) thresholded image of (b) with relative pixel intensities below 30% subtracted, showing relative up-regulation of fis indicating entry into logarithmic growth

c d

Growth in the contractile vacuole

0

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0 10 20 30 40 50 60

time (seconds)

cv diameter "salmonallae"cv diameter empty

Relative diameter of contractile vacuole in an infected and uninfected amoeba

μm

A. polyphaga and S. typhimurium, phase contrast (a) and fluorescence images (b). Up-regulation of the fis promoter in some bacterial cells contained within phagocytic food vacuoles suggests that intravacuolar growth was occurring and replication was possible

Filamentous growth of S. typhimurium

0

10

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length (um)

Frequency

Frequency

Frequency

Day 1

Day 3

Day 5

Salmonella cell length

Filamentation

•S. typhimurium formed filaments up to 500 μm long in the presence of A. polyphaga.

•Up-regulation of fis in intracellular salmonallae exhibiting early stages of filamentous growth suggests that this morphological change may be linked to passage through A. polyphaga.

•Stresses similar to those found within protozoan food vacuoles are known to cause filamentation; low hydrogen peroxide concentrations induced filamentation in E.coli(Brandi et al., 1991). Lytic compounds have produced filamentous growth of E.coli at sublethal doses (Cegielska & Taylor, 1985).

•Filamentation is also associated with swarming, ie. a possible specialisation to rapid colonisation, and has been reported in E. coli and S. typhimurium (Harshey & Matsuyama, 1994).

•The formation of grazing resistant bacterial morphotypes has been previously observed in the presence of protozoans.

Amoebae-bacteria population level interactions

1. Matrices of 100 fields of view, 2 x phase contrast with 4 second interval + 1 fluorescence image. 10 x objective, non-nutrient agar, no coverslip.

2. Time-lapse image sequences, 1 frame per minute (approx. 600x)

Spatial and temporal analysis

Spatial and temporal analysis

TRACKING

Saprophytic growth of passaged cells

Deposition of faecal pellets and colony growth

Each colony was formed from an egested food vacuole or “faecal pellet” which were deposited at regular intervals by an amoeba. This illustrates bacterial translocation, survival of digestion and subsequent growth on nutrients contained in the faecal pellet and/or secreted by the amoebae

Dissemination of viable salmonellae

Bacterial colony growth on NNA along an amoebal trail, subsequently colonised by amoebae.

Saprophytic growth of passaged cells

Summary of interactions with amoebae

•A proportion of salmonellae can survive digestion, and are egested in a pellet and disseminated

•Rapid bacterial growth occurs on pellets

•Salmonellae can infect contractile vacuoles (osmoregulatoryorganelles)

•Bacterial filamentation can occur during interactions with amoebae, possible a phenotypic change induced by ingestion and passage