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Sample Collection
Collected 1 liter of stream water from each
site.
FilterSamples were concentrated using a .45 µg
membrane filter.
CultureSmear of filter plated on McConkey Agar
with MUG.
VerificationIsolated colonies were verified as E. coli
using citrate, indole, Voges-Proskauer, and
methly red IMViC tests.
RibotypingIsolated E. coli colonies were ribotyped
using a Dupont Riboprinter©. ECORI
restriction enzyme fragments DNA, and
electrophoresis is conducted. DNA is
removed from gel via Southern blotting and
the membrane is washed by a 16s rDNA,
RNA probe.
Cluster Analysis Unweighted pair-grouping (UPGMA)
Euclidian distance method was used to
create a dendogram using Bionummerics©
software package.
IdentificationThe unknown stream samples were
compared to the known human and livestock isolates of E. coli. The highest similarity value of 92 or more indicated a match. The identification
was compared to the cluster analysis for confidence and consistency.
•Phosphorous is a key nutrient essential to life. Too much however can
cause problems in an aquatic system. These problems can include an
overload of nutrients that cause turbidity and algae blooms (1)
Phosphorous loading on a waterway is caused from a variety of factors,
and these factors are in large part due to land use .
•The three different land types concentrated on in this study were
agricultural, impervious ( urban ), and forested. The stream sections were
classified based on the predominant surrounding and upstream land uses.
•Nineteen stream sections from tributaries in the Lamoille River drainage
basin were examined in the Summer of 2008 for amounts of total
phosphorus and fecal coliform bacterial contamination.
•Total P concentrations in stream water were generally three times higher
during a period of heavy precipitation in late July than during base flow
in the middle of June. Some agricultural and impervious sites had total P
concentrations comparable to reference forested sites, but impacted
agricultural and impervious sites could have total P concentrations two to
twenty-fold higher than forested sites during base flow and storm events.
•The overall trends of the phosphorous discharge point to Agricultural sites producing the highest
amounts, followed by the impervious sites, while the forested sites show the lowest amount of daily
discharge
•The source of E. coli in agricultural areas was predominantly from livestock.
• The source of E. coli in impervious sites was also largely from livestock, but the contribution from
human sources increased to one-fourth of the isolates.
•The source of most isolates of E. coli in forested sites was unable to be determined, possibly because
wildlife were not included in the genetic library, but livestock were still the source for one-fourth of the
E. coli isolated.
• Total Phosphorus was measured on seven occasions from June 13
through August 5 for a total of 400 samples.
• Phosphorus samples were analyzed by the University of Vermont
Vermont Streams group
• Coliform and E. coli enumerated utilizing Hach coliblue24© method
• Library and unknown stream E. coli isolates were processed by
ribotyping (see below)
1.Lake Champlain Basin Program, date n/a, http://www.lcbp.org/PHOSPSUM.HTM. Retrieved on 11/1/08
2.Lamoille Valley watershed map taken from
www.lcbp.org/Atlas/MapJPEG/nat_lamoille.jpg. Retrieved on 8/5/08.
• The discharge trends illustrates clearly the areas where the state could use
more prominent buffer zones, in particularly, the agricultural sites and a
number of impervious sites.
•The frequent occurrence of E. coli from livestock (predominantly cows,
goats, horse, and sheep) reflects the pastoral nature of the landscape in
Lamoille County. As would be expected, human sources were predominantly
associated with human habitation (impervious) sites.
•Library classification of wild life, and a more extensive human E.coli library
would be beneficial, and may happen in the near future in order to help
identify the unknown samples acquired this summer and for future studies.
ABSTRACT
METHODS
RESULTS
CONCLUSIONS
BIBLIOGRAPHY
Comparison of total phosphorus and microbial source tracking by land use type in the Lamoille
River watershedGreggory A Perry, Timothy R Thurston, and Robert Genter PhD
Johnson State College, Johnson VT
RIBOTYPING RESULTS
PHOSPHOROUS DISCHARGE
ACKNOWLEDGMENTS
For funding of our project we thank the NSF and VT
EPSCoR. KathiJo Jankowski for an amazing job coordinating the streams project, and the
laboratory team at UVM, who were instrumental in processing our phosphorous samples.
Jim Ryan whom is part of the Vermont Department of Natural Resources played a vital role
in helping us choose our sites. We also thank Farley Ann Brown, Declan MaCabe, and
Carlos Pinkham for advice and inspiration.
**Values of zero notate either values too small to
record, or incomplete processing of samples.
0
2
4
6
8
10
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14
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20
40
60
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100
120
140
Dis
cha
rge
m3
Co
nce
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ati
on
µg
/l
Brown's River AG
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Brewster River F
0
5
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15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Brown's River F
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Brewster River S IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Brewster River IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Deer Brook Ag
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Deer Brook IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
French Hill Brook F
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Brown's River IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Ryder Brook IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Gihon River IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Mill Brook IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
North Branch IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Mill Brook AG
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Wild Branch IMP
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Wild Branch AG
0
5
10
15
20
25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Wild Branch F
0
5
10
15
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30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
Seymour Brook AG
0
5
10
15
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25
30
0
20
40
60
80
100
120
140
Dis
char
ge m
3
Conc
entr
atio
n µg
/l
North Branch F