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Data Analysis for Source ID:Examples of Statistical Methods and Results

Julie Kinzelman, City of Racine

Beach Management Workshop

April 14 – 15, 2005, Egg Harbor, WI

Association of Bacterial Indicator Levels to Coastal

Conditions

Can we tell when E. coli will be elevated?

Potential Associations

• Wind Direction

• Wave Height Estimation

• Precipitation

• Surface Water Temperature

• Presence of Algae

Wind Direction

Wind Vector Containing Direction East

YEAR NUMBER OF DAYS INCLUDING WIND VECTOR EAST (90°)

May June July August

2002 0* 10 9 16

2003 1** 9 12 17

2004 1*** 9 10 10

Number of Sampling Events

Wind Vector East vs. Bathing Water Quality Failures

y = 0.7475x + 0.1884

R2 = 0.4988

0

2

4

6

8

10

12

14

16

18

0 2 4 6 8 10 12 14 16 18

Number of Days Per Month With Wind Vector East

Nu

mb

er

of

Fa

ilu

res

Winds East = High Waves

Influence of East Wind

• In 2 out of the 3 years the increased number of days including wind vector E also reflected an increase in the number of days per month with poor water quality failures

• This translates to a correlation of ~ 50%

• Onshore winds frequently increased wave height as noted in field observations

Wave Height

Estimated Visually (low, medium, or high)

YEAR DAILY FREQUENCY OF WAVE HEIGHT BY MONTH

May/June July August/September

Low Med. High Low Med. High Low Med. High

2002 6 5 10 12 6 9 4 13 10

2003 15 13 0 6 14 5 8 11 4

2004 14 6 4 13 4 5 5 16 9

Frequency of Wave Height

0

5

10

15

20

25

30

35

40

NUMBER OF DAYS

MAY/JUNE JULY AUGUST

MONTH

WAVE HEIGHT DISTRIBUTION (DAYS/MONTH)

LOW

MEDIUM

HIGH

The number of days with moderate or high waves increased

as the summer progressed.

The total number of days designated as having high waves increased in August

Local Mathematical Model

Best Predictor:

E. coli today = 10.801 + 0.248 (yesterday's E. coli count) + 65.859 (wave height) [p = 0.009]

Second Best Predictor:

Wave Height + Easterly Wind Vector [p = 0.02]

Precipitation

Wet Weather Advisories

Average Daily Precipitation

AVERAGE DAILY PRECIPITATION BY MONTH (CM)

YEAR MONTH

JUNE JULY AUGUST

2002 0.61 0.38 0.48

2003 0.15 0.58 0.18

2004 0.58 0.08 0.33

Monthly Precipitation

MONTHLY PRECIPITATION TOTALS (CM)

YEAR TOTAL MONTHLYPRECIPITATION

SEASONTOTAL

JUNE JULY AUGUST

200212.82 9.48 12.65 34.95

20033.62 14.08 4.05 21.75

200412.50 1.78 8.80 23.08

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

PRECIPITATION (CM)

june july august

MONTH

AVERAGE DAILY PRECIPITATION BY MONTH

2002

2003

2004

0

2

4

6

8

10

12

14

16

PRECIPITATION (CM)

june july august

MONTH

MONTHLY PRECIPITATION TOTALS (CM)

2002

2003

2004

Although June had high amounts of ppt. it always had the least number of BWQF.

0

2

4

6

8

10

12

14

16

Monthly Rainfall (cm)

JUNE JULY AUGUST

Month

Monthly Precipitation Totals (cm) vs. Number of Bathing Water Quality Failures - 2002

PPT (CM)

NO. OF BWQF

2004

0

2

4

6

8

10

12

14

16

18

Monthly Rainfall (cm)

JUNE JULY AUGUST

Month

Monthly Precipitation Totals vs. Number of Bathing Water Quality Failures - 2004

PPT (CM)

BWQF

Rainfall can have an immediate impact on surface water quality

1 9 1

8 7 2

01 0 02 0 03 0 04 0 05 0 06 0 07 0 08 0 09 0 0

E . c o l i M P N /1 0 0 m l

9 0 0 1 2 0 0

T im e o f S a m p le C o l le c t io n ( 0 9 0 0 o r 1 2 0 0 )

0 8 / 1 7 / 2 0 0 4

Storm Water Discharge to Lake Michigan after Rain Event

Rainfall vs. BWQF

• Rainfall preceded about 50% of all BWQF in Racine in 2004

• The impacts of rainfall can be sudden and immediate

• Pre-emptive advisories may be appropriate• Rainfall can impact surface in a variety of

ways:– CSO, SSO, Runoff, Storm water discharge

Surface Water Temperature

Did Warmer Water = More Bacteria?

Upwelling can change surface water temperatureLake Michigan Surface Temperature (F) at North Beach, Racine, WI- Summer 2002

40

45

50

55

60

65

70

75

80

03-J

UN-02

05-J

UN-02

07-J

UN-02

09-J

UN-02

12-J

UN-02

17-J

UN-02

19-J

UN-02

21-J

UN-02

26-J

UN-02

28-J

UN-02

02-J

UL-02

08-J

UL-02

11-J

UL-02

15-J

UL-02

18-J

UL-02

20-J

UL-02

23-J

UL-02

25-J

UL-02

27-J

UL-02

29-J

UL-02

01-A

UG-02

03-A

UG-02

05-A

UG-02

07-A

UG-02

10-A

UG-02

12-A

UG-02

15-A

UG-02

19-A

UG-02

21-A

UG-02

23-A

UG-02

27-A

UG-02

Date

Te

mp

era

ture

(F

)

Wind Direction = S

Wind Direction = S

RELATIONSHIP OF E. COLI TO SURFACE WATER TEMPERATURE - 2004

y = 0.0629x - 2.6058

R2 = 0.0379

-2

-1

0

1

2

3

4

5

50 55 60 65 70 75 80

TEMPERATURE (F)

E.

CO

LI

MP

N/1

00

ML

(L

OG

10

)

Scatter plots of the data demonstrate that a strong

correlation did not exist between E. coli and surface water

temperature [R2=0.04(2004)]

Algae (Cladophora)

Was there more E. coli when there was more algae?

High Amounts of Algae - 2002

Low Amounts of Algae - 2004

ALGAL PRESENCE VS. E. COLI CONCENTRATION

0

0.5

1

1.5

2

2.5

3

3.5

0 0.5 1 1.5 2 2.5 3 3.5

ALGAL PRESENCE

Association of Algae to BWQF

• The concentration of E. coli isolated from North Beach did not correlate with the amount of algae noted in the field at the time of collection

• Neither was there a higher incidence of water quality advisories on days when moderate or high levels of algae were noted

Association of Algae to BWQF

• E. coli concentration, ranked by code relating to Cladophora presence and subjected to ANOVA showed no significant difference (p = 0.64)

• Limited by the small number of degrees of freedom (n = 27)

• Correlation may have been noted if the degrees of freedom were higher, i.e. more samples collected

Best Predictors of Water Quality in Racine, WI

• Wave Height (> 1.0 ft.)

• Wind Direction (East)

Acknowledgements

• S. C. Johnson, A Family Company

• WI DNR

• Richard Whitman, USGS

• City of Racine Health Department

• University of Surrey, RCPEH

Too Many Statistics!!!

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