OLTAC Meeting - Oct. 31, UPSTATE FRESHWATER INSTITUTE
OLTAC Meeting - Oct. 31, 20122
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OLTAC Meeting - Oct. 31, Summer average TP = 20 µg/L
OLTAC Meeting - Oct. 31, minor bloom > 15 µg/L Summer average Chl-a = 6.5 µg/L
OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31, summer average = 2.0 meters
OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31, Nitrate – hypolimnetic composite Soluble reactive phosphorus – 15 meter sample
OLTAC Meeting - Oct. 31, Percent of monthly geometric means <200 cfu/100ml
OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31, Metro 001 Outfall was in full compliance with ammonia and phosphorus limits Tributaries were largely in compliance with AWQS, with the following noteworthy exceptions: Excursions of the standard for fecal coliform bacteria were widespread Water quality standards for pH, ammonia, and nitrite were exceeded at Allied East Flume Water quality conditions at South Deep met most standards, with the following exceptions: Dissolved oxygen in the lower waters Total dissolved solids Nitrite (at 12 meters on 2 dates) The standard for fecal coliform bacteria was exceeded at a single nearshore sampling site near the mouth of Onondaga Creek
OLTAC Meeting - Oct. 31,
Meteorological Conditions OLTAC Meeting - Oct. 31,
Total Phosphorus and Chlorophyll-a Concentrations in the Upper Waters OLTAC Meeting - Oct. 31, Summer average = 21 µg/L (to date) Summer average = 5.2 µg/L (to date)
Compliance with SPDES Permit Limits OLTAC Meeting - Oct. 31,
Secchi Disk Transparency OLTAC Meeting - Oct. 31, Summer average = 2.0 m (to date)
Dissolved Oxygen Patterns OLTAC Meeting - Oct. 31,
Regulation of Sediment P Release by Nitrate OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31, Assessing Compliance with the AWQS for Fecal Coliform Bacteria Percent of monthly geometric means <200 cfu/100ml (April-August 2012)
Assessing Compliance with the Swimming Safety Guidance Value (Secchi disk >4 ft. or 1.2 m) OLTAC Meeting - Oct. 31, April-August 2012
Time Series of Specific Conductance Values Versus 10-Year Average OLTAC Meeting - Oct. 31,
Chloride and Total Dissolved Solids Concentrations in the Metro Effluent OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31, Color Contours of Specific Conductance and Nitrate - Near the Metro Outfall
OLTAC Meeting - Oct. 31, Color Contours of Specific Conductance and Nitrate - at South Deep
Recent Vertical Profiles at South Deep OLTAC Meeting - Oct. 31,
OLTAC Meeting - Oct. 31,
Time Series of Fecal Coliform Counts in Onondaga Creek, OLTAC Meeting - Oct. 31,
Annual Average Fecal Coliform Counts - Onondaga Creek OLTAC Meeting - Oct. 31, Dry weather defined as less than 0.08 inches of rainfall over the preceding 60 hours
OLTAC Meeting - Oct. 31, Trend analysis is complicated by extreme temporal variability (>5 orders of magnitude), uneven intensity of sampling, and potential effects from multiple management actions (gray and green infrastructure projects) A more rigorous analysis will be included in the 2012 AMP Report data: Onondaga Creek, Harbor Brook, Ley Creek, Ninemile Creek Conduct power analyses to establish realistic expectations Consider trends other than monotonic trends (e.g., step changes) Assess seasonal variations Look at alternate thresholds for dry and wet weather conditions Explore potential covariates (e.g., flow, temperature, phosphorus)
OLTAC Meeting - Oct. 31, Appropriate application of the AWQS for fecal coliform bacteria Sampling frequency Wet weather samples NYSDEC Water Quality Standard for Fecal Coliforms: “The monthly geometric mean, from a minimum of five examinations, shall not exceed 200 per 100 mL”