Assessment of Microbial Indicators for Monitoring
Recreational Water Quality in Marine Sub/Tropical Environments
(Recreational Microbes)
Principal Investigators: Helena
Solo-Gabriele Ph.D. and John
Wang Ph.D.
Collaborating Principal Investigators: Kelly
Goodwin PhD (NOAA-AOML),
Jay
M. Fleisher, PhD (Nova Southeastern University)
Co-Investigators: Lorraine Backer, Samir
Elmir, Jack
Fell, Lora Fleming, Peter
Minnett, Carol Palmer, Eugene
Rankey
Participating Facilities Cores: Remote Sensing and Genomics
Abstract
Microbial water quality indicators are found in high concentrations
in sewage, and are thus used to determine whether or not a
water body is safe for recreational purposes. Recently, concerns
have been raised about the appropriate use of microbial indicators
to regulate recreational uses of water bodies. This is particularly
true for water bodies located in tropical and subtropical environments,
due to the potential for microbial regrowth in these latitudes,
and the fact that studies used to set national guidelines were
not conducted in tropical and subtropical environments. The
primary goal of this study is to evaluate the relationship
between human health and the physical and microbial characteristics
of a coastal body of water and its shoreline. This goal is
addressed by measuring human health effects and microbial water
quality at a recreational beach site within a subtropical climate,
and by developing a predictive, coupled model of hydrodynamic
characteristics and microbial fate that can be used to distinguish
impacts from sewage sources versus re-growth of microbes.
Each of these sources could possibly result in different health
effects as observed at the beach site. Substantial pilot data
have been collected for the subtropical study site chosen for
this research. These pilot data, as well as the literature,
indicate that exposure to contaminated recreational marine
waters may result in human health effects, and that the shoreline
sediments are one likely source of indicator microbes. Human
health is evaluated in the project through an epidemiologic
study that randomly assigns exposure to water or beach with
coordinated individual environmental sampling and repeated
follow-up of reported human health effects. Water quality is
evaluated through two sets of environmental measurements. The
first phase of the environmental assessment focuses on identifying
the distribution and sources of enterococci (the current, federally-recommended
indicator microbe) within the study site. Enterococci is monitored
through an intensive effort aimed at identifying sources, in
particular shoreline sources, and correlations with suspended
sediment concentrations. The data gathered from this intensive
sampling effort will be used to develop source functions for
an enterococci fate model to be coupled with a hydrodynamic
oceanographic model developed for the area. The coupled enterococci
model will be used in a predictive fashion to determine when
and where within the study beach the epidemiologic study should
take place to evaluate baseline levels of the indicator due
to regrowth. These baseline levels will be compared with
measured concentrations in the water column to identify time
periods that may be impacted by sewage. The second phase of
environmental measurements will focus on the analysis of multiple
microbes coincident with times that participants participate
in the epidemiologic study. Microbe measurements will include
traditional (enterococci, Escherchia coli , fecal
coliform) and non-traditional ( Clostridium perfringens ,
coliphage) microbial indicators, as well as direct measurement
of microbial pathogens ( Staphylococcus aureus , enterovirus,
Norwalk virus, hepatitis A, Cryptosporidium parvum ,
and Giardia lamblia ). Analysis of the viral and protozoan
pathogens will include traditional PCR and Rresults from microbe
analysis will be crosschecked against new Luminex technology.
A primary goal of this research is to develop a rapid (same
day), accurate high throughput and sensitive molecular test
for the identification of pathogenic microorganisms in marine
and freshwater environments. The Remote Sensing Core and the
Genomics Core will participate in this interdisciplinary collaborative
research study.
The results from the coupled hydrodynamic and microbial fate
model will be compared with the pathogen and human health data
for the purposes of predicting beach closures due to health
hazards. Ultimately, the human, environmental and oceanographic
data will be used to develop a predictive model with broad
applicability to beaches in the tropics and subtropics with
appropriate modifications for local conditions. The final result
will be the improvement of recreational water quality monitoring
in tropical/subtropical marine environments, and an increase
in public confidence in the results from microbial water quality
monitoring and modeling.
Specific Aims and Hypotheses.
The primary goal of this study is to evaluate the relationship
between human health, and the physical and microbial characteristics
of a coastal water body and its shoreline. This relationship
will be evaluated by comparing reported human illnesses with
microbial water quality within a subtropical environment and
by evaluating whether re-growth of the currently recommended
indicator microbe (enterococci) is responsible for a significant
proportion of the microbe burden within a beach and its associated
water body. The relationship between environmental and sewage
sources of contamination will be evaluated through a coupled
hydrodynamic/water quality model that includes a fate component
to simulate microbe re-growth and die-off. The secondary goals
of this project include testing a new innovative technology
referred to herein as Luminex for rapid, less expensive detection
of indicator microbes and pathogens, and evaluating the inter-relationship
between enterococci re-growth and beach sand. Such goals will
be addressed through interdisciplinary research that includes
physical oceanographers, environmental scientists, and biomedical
experts.
This research project is innovative in that it evaluates
the relationships between marine processes (water circulation
and contaminant transport) and public health (reported illness
at a beach site) in a subtropical area. It is an interdisciplinary
study involving public health professionals (from the University
of Miami Medical School, University of Florida College of Veterinary
Medicine, Miami-Dade Department of Health, and Centers for
Disease Control and Prevention [CDC]) and researchers (from
the University of Miami Marine School and College of Engineering)
that focus on environmental monitoring and ocean process modeling.
The epidemiologic study will address a number of shortcomings
characteristic of previous studies, including assessing individual
exposure to seawater or beach sand, creating a coupled hydrodynamic/microbial
water quality model to evaluate sources of microorganisms to
the beach site, and assessing the applicability of current
microbial indicators to predict human health risks specifically
in subtropical recreational waters. The environmental monitoring
component of this study will include analysis of both indicator
microbes and pathogens, which due to its expense, are not commonly
evaluated. It is also rare for studies to evaluate both point
and non-point sources of microbes. This study will also evaluate
the suitability of a new innovative technology, Luminex, for
evaluating concentrations of indicator microbes and pathogens
in water. If this technology is found to perform well, it can
revolutionize the way in which water quality is monitored at
beach sites due to much more rapid results and lower costs
than traditional analytical methods.
These goals will be attained through the following six research
modules.
Coupled Hydrodynamic/Microbial Water Quality Model (Wang)
- Expand the capabilities of an existing hydrodynamic
and transport model developed for the study site by incorporating
microbial simulation capabilities, by expanding the model
domain to include the major point sources, and by refining
the model resolution at Hobie Beach. The results from this
model will be used to guide the field sampling plan as to
when and where within the study site the epidemiologic study
should occur and when/where samples should be collected during
the epidemiologic study. Within the larger context, the aim
is to develop this model as a predictive tool for establishing
beach closures.
Intensive Environmental Monitoring of Enterococci (Solo-Gabriele/Elmir)
- Update sanitary survey for site. Develop sample collection
program for evaluating sources of enterococci (current microbial
indicator recommended by the federal government) within the
study site. This will involve spatially and temporally intense
sample collection in water and sand. Laboratory work will
also be included to further establish source functions needed
for the water quality model.
Sediment Study (Rankey/Solo-Gabriele/Elmir)
- Characterize sediment types and study of spatial variability
in different types of sediment. Analysis of enterococci levels
in the sediments will be coordinated with activities in the
modules above. Analyze the correlation between water column
turbidity and wind conditions. Results will be used in support
of developing source functions for suspended sediments within
the hydrodynamic model.
Epidemiologic Study (Backer/Fleming/Elmir)
- Conduct a prospective epidemiologic study to assess the
human health risks associated with swimming in subtropical
seawater contaminated with infectious microorganisms.
Microbe Monitoring Using Traditional Methods (Palmer/Solo-Gabriele/Elmir)
- Monitor water during the epidemiologic study for the numbers
of pathogens and microbiological indicators, using traditional
analysis methods. Microbes measured will include the traditional
indicators and pathogens. Microbe
Monitoring Using innovative Luminex Technology (Fell/Palmer)
- Develop Luminex technology for analyzing microbes listed
in module above. Compare results from Luminex with those
using traditional methods. Microbial monitoring will
shift towards Luminex due to the increased speed and lower
cost of analysis, if Luminex is shown to correlate with
results using traditional microbial monitoring techniques.
Publications & reports
Solo-Gabriele, H.M., Durbin, M.E., Abdelzaher, A.M., Heybeck,
N.F., Elmir, S., Goodwin, K.D., and Sinigalliano, C., 2005. Factors
that Influence Fecal Indicator Microbe Levels. Proceedings
of the Annual Meeting of the Florida Branch of the American
Society for Microbiology.
Abstract
Fecal indicator microbes have been traditionally used for
regulatory purposes to assess the quality of recreational
beach waters. The detection of elevated levels of fecal indicator
microbes are usually followed by beach closures or advisories
due to presumed health risks. However, recreational water
quality standards have been developed from studies at sites
characterized by point sources of sewage contamination, a
source known to contain human pathogens and an abundance
of fecal indicator microbes. Increasing evidence suggests
that sewage is not the only source of fecal indicator microbes
and that this group of microbes is capable of regrowth within
the environment, specifically within soils. Many researchers
have indicated that local climate plays a role in the regrowth
phenomena. Regrowth is most prevalent in freshwater systems
that are characterized by limited flushing; however, regrowth
has been observed in marine systems. The predominant characteristics
of the sediments that appear to facilitate regrowth are sediments
characterized by elevated organic content and by relatively
shallow embankments that are periodically wetted and dried
such as during storm events and varying tidal cycles. Shallow
embankments provide for a large change in surface area in
contact with the water relative to a small change in tidal
height. Regrowth thus represents an additional non-point
source of fecal indicator microbes to the environment in
addition to the conventional sewage and animal sources. Of
interest is to determine whether elevated levels of fecal
indicator microbes from regrowth are correlated with human
health. During this presentation, data will be presented
to support the observations above. Furthermore, future plans
will be described for a study focused on evaluating human
health effects from a beach site characterized by non-point
sources of fecal indicator microbes. (PDF)
M. E. Durbin, A. M. Zaher,
N. F. Heybeck, H. M. Solo-Gabriele, S. Elmir, K. D. Goodwin,
C. Sinigalliano, 2005. The Inter-Tidal Zone
is the Source of Enterococci to a Subtropical Recreational
Beach. Proceedings of the Annual National
Conference of the American Society for Microbiology.
Abstract
Repetitive advisories have been
issued at a recreational marine beach in Miami, Florida
because water exceeded regulatory limits of enterococci.
Efforts have been made to determine sources of enterococci
to the beach waters and environmental conditions that control
enterococci levels. These conditions include: proximity to
shoreline, tidal changes, sunlight, and impacts of runoff.
Three monitoring efforts were implemented: 1) transect work
which included high and low tide comparisons, 2) spatially
intensive sediment samples, and 3) hourly sampling during
a 48-hour period, including collection of runoff. Enterococci
were enumerated by traditional membrane filtration or chromogenic
substrate method. Results showed that enterococci levels
in water increased as the shore was approached. The average
level in knee deep water within a few feet of the shore (83
CFU/100 ml) was higher than the level in water 100 m from
the shore (29 CFU/100 ml). On average, levels in knee deep
water were 69 CFU/100 ml during high tide and 5 CFU/100 ml
during low tide. Sediment samples collected under water from
the inter-tidal zone during high tide had lower numbers (5,400
CFU/100 ml pore water), while sediment samples collected
during low tide from the same area but above water were higher
(23,600 CFU/100 ml pore water). The highest levels of enterococci
were measured in “dry” sediments
above the high tide line but within a few meters of the
inter-tidal zone (35,900 CFU/100 ml pore water). Microbe
levels in sediments consistently decreased away from the
inter-tidal zone. Hourly sampling showed that tides were
a more important factor than sunlight effects. Runoff water
was found to contribute water with high levels of enterococci
(14,500 CFU/100 ml). Overall, levels of enterococci were
higher in sediment samples than in water samples, and levels
were found to be more concentrated closer to the shore. These
results suggest that the wash-in of sediments and accompanying
pore waters from the inter-tidal zone play a major role in
controlling enterococci levels in recreational beach waters.
Wash-in occurs through both tidal fluctuations and runoff.
(PDF)
"Impacts of Hurricanes Katrina and Rita on the microbial landscape of the New Orleans area"
C. D. Sinigalliano, M. L. Gidley, T. Shibata, D. Whitman, T. H. Dixon, E. Laws, A. Hou, D. Bachoon, L. Brand, L. Amaral-Zettler, R. J. Gast, G. F. Steward, O. D. Nigro, R. Fujioka, W. Q. Betancourt, G. Vithanage, J. Mathews, L. E. Fleming, and H. M. Solo-Gabriele
ABSTRACT
Floodwaters in New Orleans from Hurricanes Katrina and Rita were observed to contain high levels of fecal indicator bacteria and microbial pathogens, generating concern about long-term impacts of these floodwaters on the sediment and water quality of the New Orleans area and Lake Pontchartrain. We show here that fecal indicator microbe concentrations in offshore waters from Lake Pontchartrain returned to prehurricane concentrations within 2 months of the flooding induced by these hurricanes. Vibrio and Legionella species within the lake were more abundant in samples collected shortly after the floodwaters had receded compared with samples taken within the subsequent 3 months; no evidence of a long-term hurricane-induced algal bloom was observed. Giardia and Cryptosporidium were detected in canal waters. Elevated levels of fecal indicator bacteria observed in sediment could not be solely attributed to impacts from floodwaters, as both flooded and nonflooded areas exhibited elevated levels of fecal indicator bacteria. Evidence from measurements of Bifidobacterium and bacterial diversity analysis suggest that the fecal indicator bacteria observed in the sediment were from human fecal sources. Epidemiologic studies are highly recommended to evaluate the human health effects of the sediments deposited by the floodwaters. (PDF)
Proceedings of the 2004 National Beaches Conference http://www.epa.gov/OST/beaches/meetings/2004/index.htm
S. Elmir-Miami Dade County Department of Health- Microbial
Monitoring and Epidemiologic Study at Two Beach Sites,
2004 National Beaches Conference pp. 415 & 416.
(PDF
ABSTRACT)
J. Fleisher, PhD-Nova Southeastern
University- Risk
Perception Bias and Self Reported Symptoms,
2004 National Beaches Conference pp. 301 & 302.
(PDF
ABSTRACT)
K. Goodwin, PhD-NOAA/AOML- Immobilized
DNA Probes to Rapidly Detect Toxic Dinoflagellates and
Sewage- Indicating Bacteria, 2004 National Beaches
Conference pp. 420 (PDF
ABSTRACT)
K. Goodwin, PhD-NOAA/AOML- Hybridization Based
Detection of Fecal Bacteria, 2004 National Beaches
Conference pp. 420 & 421 (PDF
ABSTRACT)
K. Goodwin, PhD-NOAA/AOML- Assay and Remote Sensor
Development for Molecular Biological Water Quality Monitoring,
2004 National Beaches Conference pp. 268-272 (PDF
ABSTRACT)
Fleming LE, Solo Gabriele H, Elmir
S, Shibata T, Squicciarini D, Quirino W, Arguello M, Van De
Bogart G. A Pilot
Study of Microbial Contamination of Subtropical Recreational
Waters. Fl J Env Health March 2004;29-33. (PDF)
Abstract
Microbial water quality indicators are used to
determine whether a water body is safe for recreational
purposes. There have been concerns raised about the appropriate
use of microbial indicators to regulate recreational uses
of water bodies, in particular those located in tropical
and sub-tropical environments.
This prospective cohort
pilot study evaluated the relationship between microbial
water quality indicators and public health within two
public beaches without known sewage discharge, but with
historically high microbial levels for one beach, in subtropical
Miami-Dade County (Florida). Monitoring was conducted in
three phases: daily water monitoring, beach sand sampling,
and spatially intense water sampling. An epidemiological
questionnaire from a Los Angeles recreational beach-goer
study was used to assess the self-reported swimming-related
symptoms and exposures. There was no significant association
between the number nor the type of reported symptoms and
the different sampling months or beach sites, although
persons who returned repeatedly to the beach were more
likely to report symptoms. The number of indicator organisms
correlated negatively with the frequency of symptoms reported
by recreational beach goers. Results of the daily monitoring
indicated that different indicators provided conflicting
results concerning beach water quality.
Larger epidemiologic
studies with individual exposure monitoring are recommended
to further evaluate these potentially important associations
in subtropical recreational waters.
Shibata T, Solo Gabriele
HM, Fleming LE, Elmir S.
Monitoring Marine Recreational Water Quality Using
Multiple Microbial Indicators in an Urban Tropical
Environment. Water Research 2004;38:3119-3131.
(PDF)
Abstract
The microbial water quality at
two beaches, Hobie Beach and Crandon Beach, in Miami-Dade
County, Florida, USA was measured using multiple microbial
indicators for the purpose of evaluating correlations
between microbes and for identifying possible sources of
contamination. The indicator microbes chosen for this study
(enterococci, Escherichia coli , fecal coliform, total
coliform and C. perfringens) were evaluated through three
different sampling efforts. These efforts included daily
measurements at four locations during a wet season month
and a dry season month, spatially intensive water sampling
during low- and high-tide periods, and a sand sampling
effort. Results indicated that concentrations did not vary
in a consistent fashion between one indicator microbe and
another. Daily water quality frequently exceeded guideline
levels at Hobie Beach for all indicator microbes except
for fecal coliform, which never exceeded the guideline.
Except for total coliform, the concentrations of microbes
did not change significantly between seasons in spite of
the fact that the physical–chemical
parameters (rainfall, temperature, pH, and salinity)
changed significantly between the two monitoring periods.
Spatially intense water sampling showed that the concentrations
of microbes were significantly different with distance
from the shoreline. The highest concentrations were observed
at shoreline points and decreased at offshore points. Furthermore,
the highest concentrations of indicator microbe concentrations
were observed at high tide, when the wash zone area of
the beach was submerged. Beach sands within the wash zone
tested positive for all indicator microbes, thereby suggesting
that this zone may serve as the source of indicator microbes.
Ultimate sources of indicator microbes to this zone may
include humans, animals, and possibly the survival and
regrowth of indicator microbes due to the unique environmental
conditions found within this zone. Overall, the results
of this study indicated that the concentrations of indicator
microbes do not necessarily correlate with one another.
Exceedence of water quality guidelines, and thus the frequency
of beach advisories, depends upon which indicator microbe
is chosen.
ASLO Conference Abstract
Baums,
I.B. , CIMAS, University of Miami, Miami, USA, ibaums@rsmas.miami.edu
Kiesling,
T., Georgetown University, Washington, USA, tlk6@georgetown.edu
Goodwin,
K.D., NOAA, Atlantic Oceanographic and Meteorological
Laboratories, Miami, USA, Kelly.Goodwin@noaa.gov
Fell,
J.W., RSMAS-MBF, University of Miami, Miami, USA, jfell@rsmas.miami.edu
DETECTION OF FECAL INDICATORS IN RECREATIONAL WATERS
USING THE LUMINEX 100 SYSTEM
Environmental research and monitoring
require fast microbial detection. High throughput identifications
of hundreds of species can be accomplished with a suspension
array technique: Luminex xMAP. That technology measures
multiple analytes simultaneously in a single reaction
vessel with probe bound, color coded, microspheres that
are laser identified with microfluidics. Target DNA is
amplified and labeled with biotin. Upon hybridization,
microspheres bearing target amplicons are classified
by their spectral addresses using a laser. Detection
of the amplicon is based on streptavidin coupled phycoerythrin
fluorescence. Fecal indicators are amplified with 5 primer
pairs in two multiplex PCR reactions. We designed probes
targeting the bacterial species and groups: Escherichia
coli, Bacteroides distasonis, Enterococci faecalis, Enterococci
faecium, the Bacteroides fragilis group and the total
coliform group. Probes are hybridized in a multiplex
format to the amplicons. The probe array is sensitive
and specific to the targets in an assay of a mixed known
cultured bacterial DNA. Using this probe array, fecal
indicators where detected in environmental seawater samples.
Traditional culturing techniques are used to verify the
presence of identified bacteria in the environmental
samples. This system enables rapid, reliable detection
of microbial contaminants in environmental samples.
Baums, I. B., Kiesling T., Goodwin K.D., and Fell J.W. 2005. Detection of fecal indicators in recreational waters using the Luminex 100 system. American Society for Limnology and Oceanography (ASLO) 2005 Aquatic Sciences Meeting 20-25 Feb. Salt Lake City, Utah (Abstract)
Presentations
“Freshwater and Coastal Bathing Areas and Indicator Microbes”. January 2005. Promoting Public Health Through Safe Water, sponsored by the Florida Department of Health and the Florida Department of Environmental Protection. Orlando, FL. Presented by Helena Solo-Gabriele.
“Recreational Microbes.” January 2005. First Annual Oceans & Human Health Center Science Symposium, Rosenstiel School of Marine & Atmospheric Sciences (RSMAS). Fairchild Botanical Gardens, Miami, FL. Presented by Helena Solo-Gabriele and John Wang.
“Development of Molecular Biological Tools for Monitoring Coastal Water Quality Monitoring.” March 2005. Sea Tech, Dania, FL. Presented by Kelly Goodwin.
“Factors that Influence Fecal Indicator Microbe Levels.” April 2005. Annual Meeting of the Florida Branch of the American Society for Microbiology. Ft. Lauderdale, FL. Presented by Helena Solo-Gabriele
“The Source of Enterococci to a Subtropical Recreational Beach is the Inter-Tidal Zone.” April 2005. Annual Meeting of the Florida Branch of the American Society for Microbiology. Ft. Lauderdale, FL. Presented by Mary Durbin
“The Inter-Tidal Zone is the Source of Enterococci to a Subtropical Recreational Beach.” May 2005. 105th General Meeting of the American Society for Microbiology, Atlanta, GA. Poster presented by Mary Durbin.
“Impact of Environmental Sources of Fecal Indicators on Water Quality in Sub-Tropical Climates of Florida.” November 2005. Sustainable Beaches Conference, Clean Beaches Council, St. Petersburg, FL. Presentation by Helena Solo-Gabriele. Abstract authored by: H. M. Solo-Gabriele, M. E. Durbin, A. M. Abdelzaher, N. F. Heybeck, J.D. Wang, S. Elmir, K. D. Goodwin, C. Sinigalliano
Abstract
Fecal indicator microbes have been traditionally used for regulatory purposes to assess the quality of recreational beach waters. The detection of elevated levels of fecal indicator microbes are usually followed by beach closures or advisories due to presumed health risks. However, recreational water quality standards have been developed from studies at sites characterized by point sources of sewage contamination, a source known to contain human pathogens and an abundance of fecal indicator microbes. Increasing evidence suggests that sewage is not the only source of fecal indicator microbes and that this group of microbes is capable of regrowth within the environment, specifically within soils. Many researchers have indicated that local climate plays a role in the regrowth phenomena. Regrowth is most prevalent in freshwater systems that are characterized by limited flushing; however, regrowth has been observed in marine systems. The predominant characteristics of the sediments that appear to facilitate regrowth are sediments characterized by elevated organic content and by relatively shallow embankments that are periodically wetted and dried such as during storm events and varying tidal cycles. Shallow embankments provide for a large change in surface area in contact with the water relative to a small change in tidal height. Regrowth thus represents an additional non-point source of fecal indicator microbes to the environment in addition to the conventional sewage and animal sources. Of interest is to determine whether elevated levels of fecal indicator microbes from regrowth are correlated with human health. During this presentation, data will be presented to support the observations above. Furthermore, future plans will be described for a study focused on evaluating human health effects from a beach site characterized by non-point sources of fecal indicator microbes.
“Beach Microbial Indicators and Pathogens in a Subtropical Non-Point Source Environment.” November 2005. Sustainable Beaches Conference, Clean Beaches Council, St. Petersburg, FL. Presentation prepared by J. Wang and presented by H. Solo-Gabriele. Abstract authored by: J D Wang, H Solo-Gabriele, M Durbin, A Zaher, L Fleming, I Baums, S Elmir, J Fleisher, K Goodwin
Abstract
Waters used for swimming and other recreational purposes where primary contact takes place must be of suitable quality to insure that the user is reasonably free from risk of contracting disease resulting from such contact. The timely closure of beaches when it is likely that bathers would be exposed to a health hazard is based on regular monitoring of beach water for indicator organisms. Several studies have shown that the presently used indicator organisms: enterococci and Fecal Coliforms may often lead to unnecessary closures or may not provide the early warning required. Under worst case scenarios serious economic consequences or unexpected health hazards could result. The presence of pathogenic organisms in recreational waters is thought largely to result from the introduction of human and/or animal sewage into the waters. Assessment of the risk of a person becoming ill when swimming in waters containing sewage is an extremely complex task that depends on the survival rates of various pathogens in the receiving waters and the route of exposure. For convenience, an ”indicator organism,” that is always present in sewage, is often used to signal the presence of sewage contamination and thus the possibility of pathogens being present. Limits of indicator organisms have been established based on studies that related the number of indicator organisms present at a particular location to risk of disease in people bathing at that location. Recent research has, however, questioned the use of indicator organisms as a health indicator where no known point source of sewage pollution can be identified, particularly in sub/tropical marine recreational waters. This research has questioned the appropriateness of the use of indicator organisms as a measure of health risk. Developing a better warning system, a management problem for sustainable beaches, could have substantial human health and economic benefits. One of the relatively heavily used public beaches close to the City of Miami has no point sources of sewage close enough to impact it on a regular basis. However, water samples collected by the Health Department frequently contain relatively high numbers of indicator bacteria and at times exceed EPA standards. The Oceans and Human Health Center of the University of Miami is pursuing research at this beach to clarify the usefulness of accepted indicator organisms as a warning tool in view of evidence that these organisms may survive and multiply in the sands of subtropical beaches. In one component of this research project supported by NIEHS and NSF we are developing molecular probes to rapidly and economically determine the presence of indicators and pathogens, and we are adapting the Luminex XMapTM system to provide high-throughput, multi-plexed analysis. Another component of our research seeks to understand the environmental factors that support the regrowth of indicator organisms in the beach sand and cause the ultimate transport of organisms into the water column. Yet another component aims at determining the source of the indicator organisms using source tracking techniques as well as video monitoring of beach usage to establish loads from humans and animals, such as dogs and birds. Finally an epidemiological study is being planned to determine the risk to bathers as a function of indicator organism concentrations and levels of proven pathogens in the water. Integrating this information with a suite of environmental data on temperature, wind, rain, radiation, tides, water currents and turbulence, etc. into a predictive model will not only improve our understanding of possible health risk of non-point sources of pollution but will enable more reliable assessment of the day-to-day health risk to bathers.
“The Impact of Bathing load and Beach Sand Transported by Bathers on the Microbial Water Quality of Recreational Waters.” November 2005. Sustainable Beaches Conference, Clean Beaches Council, St. Petersburg, FL. Presentation prepared by S. Elmir.
Abstract
Limited data exists concerning the concentrations of enterococci and Staph. aureus contributed to the water column in recreational water bodies by bathers, a non-point source. USEPA recommends the use of enterococci to measure the microbial water quality in marine waters. Staphylococcus aureus is a pathogen found on people’s skin, nose, and mouth and can be transmitted through open wounds and skin abrasions. The purpose of this study is to review the design, implementation, and results of two field experiments to estimate 1- the concentrations of enterococci and Staph. aureus shed by bathers and 2- the amount of beach sand and the corresponding concentration of enterococci that can be transported by bathers into the water column. The first and second experiments are called the “Big” and “Small” pool experiments respectively. The study site is “Dog” Beach located in Miami Dade County, Florida, a subtropical environment and located within the southern portion of Biscayne Bay. There are no fecal point sources present at Dog beach. The big pool experiment involved 10 volunteers who immersed their bodies in the inflatable pool for 4, 15 minute cycles with volunteers exposed to beach sand in cycles 3 and 4. Volunteers immersed their heads 3 times during each cycle. The pool was sanitized and filled with off-shore ocean water after each cycle. The off-shore ocean water was characterized by microbe levels below the detection limit. For the small pool experiment 5 volunteers were exposed to beach sand for 30 minutes before they individually entered a small tub. Each individual was rinsed with clean off-shore ocean water while in the tub. After each rinse, sand and rinsed water were collected and analyzed for enterococci. Results showed that: 1-bathers shed considerable concentrations of enterococci and Staph. aureus, 2- concentrations of Staph. aureus shed were significantly higher than enterococci, 3- significant decrease in shedding of both Staph. aureus and enterococci between cycles in all four cycles, and 4- significant amount of sand can be transported by bathers into the water column. In conclusion, bathing load as a non-point source contributes significant concentrations of enterococci and Staph. aureus to the water column, thus bathing load should be considered as one of the main non-point sources when designing recreational water quality models, and future studies are needed to validate and refine such models.
“Adaptation of the Luminex 100 System to Use in Recreational Waters.” November 2005. Sustainable Beaches Conference, Clean Beaches Council, St. Petersburg, FL. Presentation prepared by K. Goodwin. Abstract authored by: I. B. Baums, T. Kiesling, K.D. Goodwin, J.W. Fell.
Abstract
The Luminex 100 System is a suspension array technique that allows rapid, high-throughput, multiplexed detection of targets, which holds promise for detection of microbial contaminants in recreational waters. We have designed a set of primers and probes for the Luminex system to allow simultaneous detection of a variety of fecal-indicating bacteria. The probe array is sensitive and specific to targets present in a mixture of known bacterial DNA and targets have been detected in environmental samples. Luminex results are compared to culture techniques and DNA sequencing, with particular emphasis on Bacteroides.
“Recreational Microbes and Environmental Monitoring Results.” January 2006. Second Annual Research Symposium of the University of Miami Oceans and Human Health Center, Key Biscayne, FL. Presented by Helena Solo-Gabriele and John Wang.
"Efforts to Process Coastal Water Samples for Downstream Molecular Analysis" K.D. Goodwin, C. Garcia, J.A. Bonilla, T.D. Bonilla, D. Wanless, A. Abdelzaher, M.J LaGier, H. Solo-Gabriele. (Poster)
ABSTRACT
Molecular techniques offer a powerful tool for detecting
microbial contaminants. However, sample concentration is
necessary to achieve detection of fecal indicators and human
pathogens in coastal water samples, despite the sensitivity offered
by molecular methods. Bacterial targets of interest are rare in
comparison to indigenous populations; therefore, methods of
concentration based on size exclusion produce samples
containing large amounts of nontarget organisms. Concentrationof PCR inhibitors results in diminishing returns, resulting in a
concentration conundrum – increasing the level of concentration
often reduces the likelihood of achieving detection. Recovery
efficiencies tend to be low for concentration protocols and the
nucleic acid extraction and purification steps that typically follow.
Low recoveries decrease overall detection sensitivity and increase
chances that organisms of public health concern could go
undetected. Appropriate extraction controls are needed in order
to correct for losses during sample processing. The desire to
detect multiple types of organisms (e.g., protists, bacteria, and
viruses) further complicates sample processing. Furthermore,
concentration creates a process bottle-neck, interfering with
attempts to achieve rapid detection of microbial contaminants.
Strategies attempted to process coastal water samples
include membrane filtration, tangential flow filtration (TFF), virus
sorption, inclusion of extraction controls, and attempts to
streamline sample processing by eliminating the DNA extraction
step via filter PCR or PCR of crude lysate. TFF failed to provide
adequate sensitivity for both viral and bacterial targets. However,
attempts to eliminate the DNA extraction step showed promise in
cases in which PCR inhibition could be overcome. Extraction
controls showed variable recoveries ranging from 6-35%.
SPECIAL LINKS
2005 NRDC Report concerning
microbes at beaches