Thanks Peggy for the great summary.
A related issue is the possibility of aerosolized antibioics and
aerosolized antibiotic-resistant organisms blowing downwind from CAFOs
and their subsequent impact on human health. This issue was mentioned,
but not elaborated on in the Environmental Protection Commission Air
Quality Report previously discussed here. On the ARS website:
http://www.nsric.ars.usda.gov/Research.html
a research project is listed as (note Tylan is an antibiotic):
Detection and Quantification of Tylan and Tylan-Resistant Microorganisms
in Air
and Effluent that are Released from Concentrated Animal Feeding
Operations;
J.A. Zahn and L. Raskin (Dept. of Civil and Environmental Engineering,
University of Illinois)
There is an abstract (reproduced below) at:
http://www.nsric.ars.usda.gov/publications/NATL-ASAS1.pdf
which indicates a potential human health impact, "aerial transfer of
antibiotics and antibiotic-resistant bacteria from swine confinements may
represent an
important, and previously overlooked mechanism for transfer of antibiotic
resistance to humans and to the environment." I didn't see any
citations for a published paper. Interested people may want to contact
the authors (Zahn is at ARS in Ames, I think) and ask when they will be
releasing their research results and what the implications of their
research are.
Eric G. Hurley
Ames IA
~~~~~~~~~~~~~~~~~~~~~~~~
Title: Evidence for Transfer of Tylosin and Tylosin-Resistant Bacteria in
Air
from Swine Production Facilities using Sub-Therapeutic Concentrations of
Tylan
in Feed J.A. Zahn, National Swine Research and Information Center,
USDA-ARS,
2150 Pammel Drive, Ames, IA 50011.
Published abstract presented at the International Animal Agriculture and
Food
Science Conference, July 24-28, 2001, Indianapolis, IN.
Technical Abstract:
Macrolides are an important class of antibiotics used in human and
veterinary
medicine for therapy and prevention of diseases caused by Gram-positive
bacteria, and as animal growth promotants. Tylosin belongs to the class
of 16-
membered macrolide antibiotics, and has been used exclusively in
veterinary
medicine for treatment of animal diseases or for enhancing animal growth
rate.
Antibiotic resistance studies have recently focused on measuring tylosin
residues and tylosin-resistant bacteria (TRB) in animal products or in
effluent
streams from animal production facilities as potential routes for
transfer of
antibiotic resistance to humans. However, these studies have not
considered
aerial transfer from point sources as a significant route in human
exposure.
This study quantified the concentration of tylosin and TRB in air from
three
mechanically ventilated swine (finisher stage) confinements using tylosin
at
sub-therapeutic concentrations (20 g/ton) in feed. Tylosin residues
and
culturable bacteria in air at exhaust fans were trapped on absorbent
resins or
impinger samplers, respectively. Tylosin concentration was determined by
high-
performance liquid chromatography-electrospray tandem (MS-MS) mass
spectrometry
following solvent desorption of absorbent resins. The number of
culturable
bacteria and culturable, TRB were determined by plating on standard
plate
count agar containing no tylosin or 50 µg*ml -1 tylosin, respectively.
The mean
concentration of TRB (49,400 ± 16,700 CFU*m -3 ) accounted for
approximately
80% of the total culturable bacteria (62,100 ± 18,300 CFU*m -3 ) present
in air
streams from confinements, with Corynebacterium the predominant genus of
TRB.
The mean concentration of tylosin in the air from the three confinements
was
shown to be 8.1 ± 5.3 ng*L -1 of exhaust air. Feeder operation,
ventilation
rate, and animal activity were shown to be the most significant variables
influencing emission rate of tylosin and culturable TRB from the swine
confinements. The results indicate that aerial transfer of antibiotics
and
antibiotic-resistant bacteria from swine confinements may represent an
important, and previously overlooked mechanism for transfer of antibiotic
resistance to humans and to the environment.
At 06:20 PM 3/7/2002 -0600, you wrote:
Microbial
tools for tracking the source of E. coli contamination
By Nancy Hall, University Hygenic Lab
Escherichia coli is found in both human and animal
intestines. It is the predominant fecal coliform bacterium, and an
indicator of fecal pollution. Its presence indicates that disease
producing organisms may be present, but does not determine whether the
source is animal or human.
Watershed management can reduce fecal loading. This is a
prerequisite for remediation plan formulations. In the past there have
been beach closures in 5 of 35 Iowa state parks.
She described the methods that have been used for detection, and the
early attempts to differentiate the source. One was a fecal coliform to
fecal streptococci ratio. This is inaccurate because one of the organisms
persists longer in the environment. There is a need for source
(animal species) tracking methods.
She then talked about the methods of source tracking.
Bactgeriophage typing a virus that infects bacteria. This typing
scheme has four groups: serotypes 1 and 4 indicate animal feces,
serotypes 2 & 3, human and pig feces.
Genotyping is the nucleic acid probe technique. Group 1 includes
both human and animal, Group 2 humans in North America, Group 3 includes
humans in other parts of the world and Group 4 is primarily animal.
The University of Massachusetts has received a grant to use this method
to test waterways in Massachusetts and it will be interesting to see the
results.
The Toxin Gene Biomarker was developed by Betty Olson of the University
of California in Irvin. It detects the occurrence of toxin genes in E
coli using PCR technologies.
There are two kinds of E. coli that cause disease, others do not
cause disease and it is important to distinguish between them.
There are three biomarkers for toxin genes in E. coli, for human,
pig and cattle. A biomarker for bird feces is pending.
Ribotyping of E. coli automatically generates genetic
fingerprints. It is a useful tool for tracking outbreaks and for
identifying human and non human pollution. E. coli cells are lysed
and release their DNA which is cut into fragments using special
restriction enzymes. The fragments are separated by size through
electrophoresis and run through a gel. Because these fragments have
a charge they will travel at different speeds and intensity through the
gel. The pattern of the fragments in the gel is transferred from
the gel membrane, mixed with a DNA probe and chemi-luminescent chemicals
to produce a visible band pattern from which a DNA analysis can be made.
The computer software can do isolates in 8 hours.
Eight human pathogens have been collected from all over the
state. Some are the same but the animal isolates are all distinct
so that they can tell which animal they came from.
In order to do source identification they need to have a database
of known patterns they can work from to compare with the sample they are
testing. A small sample size is not as accurate as a larger sample
because it is prone to bias. The process is expensive. The cost is a
minimum of $100 per isolate and some want to screen 500 isolates.
Recent published Ribotyping studies indicate that correct classification
of samples is in the 90% range, but when all sources are grouped the
percent came down to 74%.
In a park service study half of the E. coli were not identified,
however they were able to identify seven waste sources.
In summary she said that all source tracking methods have strengths and
limitations, we need better criteria and the methods continue to
evolve.
A tool box approach to the problem is advocated, using watershed
evaluation, key monitoring parameters, strategic monitoring sites and
microbial and chemical tracking tools.
Cephalosporin resistant E. coli
Patricia Winokur, Dept. of Internal Medicine, Iowa City
A project studying Cephalosporin Resistant E coli in Iowa started in 1999
and has continued for three years.
84.2% of antibiotic use is for livestock and only 12.8% for human
use. In livestock, therapeutic uses account for 24.5
million, therapeutic uses, 2 million.
Data around the world suggests that antibiotic resistant organisms are
being transferred from animals to humans. In Europe Vancomycin
resistant Enterococci were found in animals. Then humans were found
to be carrying the same antibiotic resistance.
A story in the New England Journal of Medicine told of a Quinolone
resistant Campylobacter in Missouri from poultry products and humans with
identical molecular typing. There are absolutely identical products
in poultry products, so it has been shown that these bacteria can
transfer back to meat products.
There are now Quinolone resistant salmonella .
These bacteria can be transferred by direct contact between animals and
man. There is also food-borne transmission of resistant bacteria,
and environmental contamination.
How the environment may play a role is unknown Data is being acquired to
trace this transfer from the farm to the human.
Tetracycline resistance has been found in swine production
facilities. The resistant genes have been identified in lagoons and
traced to ground water up to 250 miles downstream from the lagoons.
The resistance has also been found in soil bacteria and groundwater is a
potential source of transmission.
In 1999 Cephalosporin resistant E. coli and salmonella were found
in hogs, cattle and humans. There are also multiple additional
antibiotic resistances.
A map of E. coli isolates shows that they are found all over
Iowa. There is a clustering of human isolates in North East
Iowa and some in or near the Quad Cities.
All of these isolates had the CMY2 resistant gene. It is present in
plasmids which are easily transferred from organism to organism because
the plasmid doesn’t have a species boundary.
This same human Celphalosporin resistant isolate has been identified in
14 different states. Retail ground meat products with Cepahlosporin
resistance have been found in Washington, D.C. stores
In addressing the question of whether Iowa waterways are a source
for transferring resistance from farm to farm, she collaborated with
Nancy Hall and the Iowa DNR. They sampled 62 sites, concentrating
on eastern Iowa. They found that between 2 and 7.1% of the E.
coli were resistant. The prevalence of resistant bacteria
in sick animals is 15.6%.
Over 70% of the resistant bacteria encode the CMY2 gene and determined
that it is being spread through waterways.
These bacteria demonstrate co-resistance. In addition to being
resistant to Cephalosporin, they are 100% resistant to Chloraphenicol,
Sulfamethoxazole and Streptomycin. They were resistant to other
antibiotics at a lower percentage.
Then they began the molecular typing of CMY2 plasmids.
They want to know how persistent the contamination is. They plan to
target sites with multiple episodes and go back and sample on a daily
basis. They would like to find particular facilities and look at
farm soil samples, and learn what the climatic events were.
Conclusion: Cephalosporin resistant E. coli is present in Iowa’s
surface waterways. The expanded spectrum Cephalosporins are the
drugs of choice for empiric therapy of gram negative infections
Some CMY 2 organisms are now resistant to most classes of antimicrobial
agents
Food-borne transfer of ant microbial resistant organisms continues to be
a concern. Water contamination may be an important mechanism from
spreading this resistance from site to site.
A question was asked about fish. She said she does not know about fish
but would expect it to be in the gut. The reason it is in ground meat is
because of fecal contamination. With non-ground meat if you sear it
on the grill that will kill it.
Fresh manure will transfer this to the water system. If it dries
out it will die. Getting rid of it will be difficult. In the
absence of antibiotics they will persist for a year.
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