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“We need a better understanding of how water and different types of pollution move and interact, while passing through
river basins towards the sea”.
Source: UK Environment Agency 2005
Introduction to MST
Outline
• Composition of faecal pollution • What is sewage? • Transmission of faecal pollution • Sources and detection of faecal contaminants •Why understanding sources of pollution is important •Microbial Source Tracking (MST) • Current research and recent developments • Where and what next?
What is sewage?
Organic particles
Micro-organisms (pathogens) Inorganic particles
Emulsions
Water
Gases (H2S, CO2, CH4 etc)
Toxins
Soluble organic material
Animals
Macrosolids
One gramme of faeces may contain: 10,000,000 viruses 1,000,000 bacteria 1,000 parasite cysts 100 parasite eggs
Micro-organisms (pathogens)
Water quality is currently monitored in EU using two groups of faecal indicator organisms
Isolated from the faeces of all warm-blooded mammals
Indicate presence of faecal contamination
• Faecal coliforms
• Intestinal enterococci
However, they do not indicate where the pollution is coming from and can take up to 48 hrs to get result!
Major Sources of Faecal Pollution
RSPB survey of five most common species of gull estimates 543,500 breeding pairs in UK.
Equivalent impact on water quality as two human adults (faecal bacterial load per day).
Seagulls (Larus spp.)
Equivalent to over 2 million humans (or entire population of Wales) defecating every day!
Understanding sources of contamination is important because:
• It helps target mitigation methods more effectively
• It helps establish responsibility/liability
• It improves understanding of the risks to human health
• It improves understanding of the risks to the environment (habitat loss, biodiversity etc)
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Microbial Source Tracking (MST)
Seagull
Pig
Cow
Deer
Human
Dog
Livestock
Wildlife
Human
Decr
easi
ng r
eso
lution
Theoretical scenarios describing levels of discriminatory resolution possible with source tracking technologies
1
2
Non-human
Human
Non-human
Human
Decr
easi
ng r
eso
lution
3
4
Microbial Source Tracking (MST)
Long-chain alkylbenzenes (detergents)
Antibiotic resistance profiling
Target organisms (Bifidobacteria, Clostridium)
Molecular methods (PCR, PFGE, MLST, Ribotyping)
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Caffeine
Carbon source utilisation
Fluorescent whitening agents
Ratio Faecal coliforms
Faecal Strep
FC:FS
Bacteroides
• Anaerobic bacteria that constitute the most substantial portion of the human gut flora
• Bacteroides don’t survive for long outside the human body (e.g. in the environment)
• However viruses (phage) which infect Bacteroides do survive outside the human body
• Present at high numbers in the faeces of humans (1010-1011 cells/gram)
• Presence of these phages in wastewaters, and in surface waters, shellfish, and sediments suggests human faecal contamination
Bacteriophage
• Have very narrow host ranges
• More persistent in the environment than bacteria they infect
• Virus capable of infecting bacteria
• Bacteriophage comes from Greek “Bacteria-eater”
• Potential indicators source
• Capable of surviving sewage treatment processes
Bacteria
Bacteriophage
• Capable of bio-accumulating in shellfish
Method of action Bacteriophage Lunar landing craft
(b) Injection of phage DNA into cell
(d) Multiple phage progeny produced
(c) Phage synthesis begins
(e) Cell lysed (burst) and phage released
(a) Attachment to cell wall
Bacteroides strain GB-124 was isolated from influent at Scaynes Hill STW, East Sussex in early 2005.
X
Population Equivalent* = 37,327 *Courtesy of Southern Water
Scaynes Hill sewage treatment works
X = Haywards Heath
Why Haywards Heath?
Enumeration of bacteriophages*
Methodology:
Grow bacterial host in broth (Bacteroides GB-124)
Step 1
Results expressed as plaque forming units (PFU) per 100 ml
Mix host with sample in semi-solid agar and pour onto agar plate
Step 2
*In accordance with ISO 10705-4. Water Quality. Detection and Enumeration of Bacteriophages-Part 4.
Incubate anaerobically for 18-24hrs at 37 oC, count zones of lysis (plaques)
Step 3
Municipal wastewaters and faecal material from pooled animal sources were tested for the presence of a range of faecal organisms/indicators including Bacteroides GB-124
Spatham Lane (< 0.5km downstream of Ditchling STW)
Wales Farm (directly downstream of farm)
Log10 PFU/100ml
Description n Mean Range % Positive
STW (final effluent) 45 sites 152 4.20 4.70 - 2.00 100
River < 0.5 km d/s of STW 55 3.65 4.30 - 2.48 100
River < 2.0 km d/s of STW 55 3.12 3.90 - 2.00 100
River >2.0 km d/s STW 194 2.38 3.63 - <DT 56
River directly d/s of farm no
STW
55 1.15 2.48 - <DT 12
River close to origin 25 ND - 0
Animal samples 45 ND - 0
Table 1. Numbers of bacteriophages infecting GB-124 in samples from different sources (n = 581)
STW = Sewage treatment works; PFU= Plaque Forming Units; ND= Not Detected; <DT = Below Detection Threshold (1 PFU/ml)
Fig 1. Mean levels of each parameter during different stages of treatment at ‘Site A’ (n=30)
• Do GB-124 phage bio-accumulate in bivalve molluscs? • If so where? • Is there a seasonality to their presence? • Is their presence linked to that of human pathogens? • If so what does it all mean?
1
10
100
1000
10000
100000
18/11/10 26/2/11 6/6/11 14/9/11 23/12/11 1/4/12
PFU
/10
0g
or
RN
A c
op
ies
/g
Date
GB124 phage and Nv concentrations in mussels from the R. Ouse (Feb 2011 to Jan 2012)
GB124 Mussel Flesh PFU/100 g
NOROVIRUS copies/g
R² = 0.4452
0
2000
4000
6000
8000
10000
12000
14000
0 200 400 600 800 1000
Nv
cop
ies/
g (G
I+G
II)
GB124 phage PFU/100g
GB124 phage (mussel flesh) vs. Norovirus (Nv) copies/g
R² = 0.8105
0
5000
10000
15000
20000
25000
30000
35000
40000
45000
0 20000 40000 60000 80000 100000
Nv
cop
ies/
g (G
I+G
II)
GB124 phage PFU/100g
GB124 phage (mussel flesh) vs. Norovirus (Nv) copies/g
Extreme event!
• Strong human signal • Elevated risk to human health (presence of human viral pathogens)
Results
• GB-124 phages present in 100% of sewage samples from 10 countries (n = >200)
• Phages infecting GB124 were not detected in any animal samples and were seldom found downstream of farms
• Highest counts found in wastewater & river samples downstream of STW (>500 PFU/ml)
• All samples positive for pathogens (adenovirus and/or norovirus) were also positive for GB-124 phages
• GB-124 phages, pathogens (adenovirus and norovirus) absent from all the non-human faecal samples
A toolbox approach Different methods for different applications (e.g. Drinking water, shellfish waters)
No single method suitable for all situations
Different cost implications
Depends on the level of detail we require (resolution)
Different methods for different geographical regions
Conclusion
Library independent (potentially culture independent)
Quantitative (results expressed PFU/100ml)
Low-cost (compared to other MST methods)
Possible to analyse multiple samples per day (e.g. 100+)
Ease of detection (method can be carried out in the field)
Phage behaviour more similar to enteric viruses than
traditional bacterial indicators (better indicator of risk)
Thanks for your attention!