<<

Water Quality in the : Indicators of Watershed Health

Tyler Spillane Stephan Zeeman, PhD Shelby Braese, Claire Whalen, Linda Jordan, Emily Brzycki, Amanda Liebau, Allegra Tedder, Kim Malkoski, Stephen Giunta, Bailey Rahn, Megan Perry, Marissa Redding, Amanda Rosa Outline

• Water Quality • Indicator Bacteria • Population Growth • Chlorophyll • NtiNutrien ts • Dissolved Oxygen • Indicator Status • Future Issues Why Monitor Bacteria?

• Indicator Bacteria: Bacteria used to measure levels of other pathogens and contaminants in

water. A Beach. http://jeskeonline.net /Pictures/Oct13/Main • Used for testing in: e%20beach.JPG – Recreational waters – SSehellfi sh ggorowin g water – Public water • Types: – coliform bacteria: • Escherichia coli E. coli bacteria – enterococci and streptococci http://upload.wikimedia.org/ wikipedia/ c ommons/thumb/3/32/EscherichiaColi_NI AID.jpg/250px‐EscherichiaColi_NIAID.jpg The other reason

• Indicator bacteria are just that – they indicate sources of other possible pollutants. • Mostly point source – from treated sewage discharges, but also some non‐point sources – wildlife, runoff, etc. • What other kinds of pollutants? – Pharmaceuticals, personal care products, other organic pollutants, nutrients The Saco River and Bacteria

• Watershed spans 1700 square miles • Runs through 29 towns, 3 counties, and 2 states, with 11 drainage areas.

Sampling

• Sampling – 18 sites along the river – Sampled roughly monthly since December 2010 • Somewhat more inconsistent since 2013. – Measured – • Total coliform bacteria and E. coli –very good (mostly) • Dissolved oxygen ‐ excellent • Nutrients –very good • Chlorophyll –very good Methods: Monitoring Bacteria

• Sample entire river once a month – Collect 100ml samples in sterile bottles – Samples are kept on ice until brought in for processing. • Samples are processed using the Idexx Colilert‐18© system – Most Probable Number (MPN) 2012Recreational Water Quality Criteria

US EPA OFFICE OF WATER 820‐F‐12‐058 Geometric Mean E. coli numbers

350

300

250

200 MPN Mean 150 2012 RWQC

100

50

0 123456789101112131415161718 Site Relation of Total Coliform bacteria to E. colli

25

20 y = 0.0565x ‐ 3.1215 ii

col R² = 0.5723

E. 15 ‐ mean

etric 10 mm Geo

5

0 0 50 100 150 200 250 300 350 400 450 Geometric Mean ‐ Total Coliforms Seasonal Variability

700

600

500 (MPN) 400 Winter Mean Spring

etric 300 mm Summer Geo 200 Fall 2012 RWQC 100

0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 Site

3

2 North Conway Treatment Plant

• No direct discharge to the river – Rapid infiltration to groundwater • Uses a nitrogen and phosphorus removal process Seasonal Variability

700

600

500 (MPN) 400 Winter Mean Spring

etric 300 mm Summer Geo 200 Fall 2012 RWQC 100

0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 Site 14

15 Saco River Corridor Commission

• The SRCC has collected water quality data for many years. • Some sites near the Saco/Biddeford: – Swan Pond Brook –Impaired (E. coli) – Thatc her BBkrook – IidImpaired ((burban stormwater, non‐point source) – Saco River EEtstuary – IidImpaired (CSO) Saco R. 19

Swan Pond Brook Saco R.

Thatcher Brook Saco River 19, Escherichia coli Above 2500

2000

April 1500 May s/100mL) June July (colonie August

coli 1000

E. September October Average

500

0 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 Year Swan Pond Brook 26 Escherichia coli 2500

2000

April 1500 May June

nies/100mL) Jul y August (colo

coli September

1000 E. October November Average

500

0 2002 2003 2004 2005 2006 2007 2008 2009 2010 Year Thatcher Brook 27, Escherichia coli 2500

2000

April 1500 May June

nies/100mL) July oo August (col

coli September

1000 E. October November Average

500

0 2002 2003 2004 2005 2006 2007 2008 2009 2010 Year Saco River 21, Escherichia coli Saco Yacht Club ramp 2500

2000

April 1500 May June s/100mL) ee July August (coloni

coli 1000 September

E. October November Average 500

0 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 Year Saco River Corridor Commission Results • The SRCC data also confirm the lower values upstream from Biddeford and Saco, and higher values in the estuary. • They point to localized “hot spots” in some tributaries. Bottom line

• Most of the time the E. coli along the river are below EPA criteria. • Higher levels are observed near Conway, NH and below the dam at Saco and Biddeford. • SlSeasonal trends are obdbserved wihith hig her values in summer and fall. – Spring, summer and fall around Biddeford and Saco. Relation to Population Size

25 45,000

40,000

20 35,000

) 30,000 ze ii NN S

15 * (MP 25,000 Mean

Population

Average MPN 20,000

ated Pop. Size metric 10 mm Geo

15,000 Esti

10,000 5

5,000

0 0 Sites 1‐5Sites 6‐12 Sites 13‐18 Region Location Population Growth

• To model population growth and land use changes we looked at Conway, NH, as an example. • We used IDRISI from Clark Labs and its Land Change Modeler • Using Data from 1992, 2001, and 2010 we predicte d condit ions for 2030. Conway, NH Pay attention to !

Maine

Predicting growth 1992‐2030

New Hampshire Fryeburg

1992 2001 North Conway Conway

2010 2030 predicted Gauging the Health of ’s Lakes and Ponds, New England Interstate Water Pollution Control Commission, 2010 Gauging the Health of New England’s Lakes and Ponds, New England Interstate Water Pollution Control Commission, 2010 Chlorophyll

Chlorophyll (mg/l) 35.00

30.00

25.00

20.00 µg/l) 1/4/2012

11/2/2013 rophyll oo 15.00 12/7/2013

Chl 2/2/2014 4/6/2014 10.00

5.00

0.00 02468101214161820 Site Chlorophyll – Seasonal Trend

Chlorophyll Mean for all samples 14.00

12.00

10.00 (µg/l)

8.00 Mean hyll pp 6006.00 Mean Chloro 4.00

2002.00

0.00 024681012 Month Nutrients

• Nutrients are substances required for growth – In the case of water quality, it refers specifically to plant or algae growth • The important plant nutrients are – Nitrogen • Nitrate, nitrite, ammonium – Phosphorus • Soluble reactive phosphorus Nitrate

Nittaterate 1

0.9

0.8

0.7

0.6 (mg/l)

0.5 ration tt Nitrate Mean 0.4 Concen 0.3

0.2

0.1

0 0 2 4 6 8 10 12 14 16 18 Site Phosphate Phosphate 1.6

1.4

1.2

1 (mg/l)

0.8 Phosphate Mean entration c c 0.6 Con

0.4

020.2

0 0 2 4 6 8 10 12 14 16 18 Site Nutrients

• EPA sampling 7/2/2010

TP TN Site Depth (mg/l) (mg/l) 1.00 Surface 0.0249 0.22 1.00 Mid 0.0316 0.24 1001.00 Bottom 0. 0380 0350.35 2.00 Surface 0.0216 0.21 2.00 Mid 0.0228 0.20 2.00 Bottom 0.0494 0.37 Dissolved Oxygen

14

12

10 nn 8

Oxyge 5/26/2011

6/30/2011 6 9/24/2011 Dissolved 11/6/2011 4

2

0 0 2 4 6 8 10 12 14 16 18 Site Report Summary

• Water Quality – E. coli –very good (mostly) – Chlorophyll – very good – Nutrients –very good – Disso lve d oxygen – excellen t Report Summary ‐ Caveats

• There are areas and times that show reduced water quality • Future growth may have deleterious effects unless we plan for it.

• New and legacy pollutants may be problematic – we did not measure these. Water Quality in the New England Coastal Basins, Maine, , Massachussets and Rhode Island, 1999‐2001. Robinson et. al. 2004. USGS Circular 1226. Things Not Measured

• PAHs, PCBs, pesticides, lead, mercury (and methyl mercury) Watersheds with less than 5% urbanization usually had no detections above 0.005 µg/l.

Questions?