Water Quality Monitoring Results. Angela Kilpatrick Trinity River Authority May 18, 2017
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1 Water Quality Monitoring Results Angela Kilpatrick Trinity River Authority May 18, 2017
2 Monitoring Plan and Lab Analysis Samples collected by PS staff are dropped off at CRWS lab for analysis of:. coli Nitrate, Nitrite, Total Kjeldahl Nitrogen Total Phosphorus, Orthophosphate Chlorophyll a,, QC-approved data for June to November 2016 submitted to TCQ Preliminary data presented for December 2016 to April 2017
3 valuation Criteria Analytical results were compared to TCQ s water quality standards and screening levels to determine if values exceeded criteria Site-specific Water Quality Criteria for the Village Creek-Lake Arlington Watershed (TCQ) Segment ID Parameter A Cl-1 (mg/l) SO4-2 (mg/l) (mg/l) DO (mg/l) grab minimum DO (mg/l) 24 hour average DO (mg/l) 24 hour minimum ph range coli #/100ml Temperature ( F; C) 95; 35 95; 35 Texas Nutrient Screening Levels and PA Nutrient Reference Criteria TCQ Screening Levels PA Reference Criteria Parameter Lake/Reservoir Stream Lake/Reservoir Stream a b c d NO 2 NO 3 NO 2 +NO 3 Chl-a d (mg/l) a 0.41 b 0.3 a 0.4 b (mg/l) c (mg/l) (mg/l) a 0.01 b a b (mg/l) a b a b (mg/l) (µg/l) a b 0.93 a b Reference conditions for level III coregion 29 waterbodies, upper 25th percentile of data from all seasons. Other Sources Reference conditions for aggregate coregion IX waterbodies, upper 25th percentile of data from all seasons, For nitrite, concentrations above 0.02 mg/l (ppm) usually indicate polluted waters (Mesner, N., J. Geiger Understanding Your Watershed: Nitrogen. Utah State University, Water Quality xtension. Chlorophyll a, as measured by Spectrophotometric method with acid correction.
4 Site 1 Wildcat Branch at Cravens CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/29/ < < /19/ <0.05 < < /15/ > < < /20/2016 <3 > < /9/ < < /14/2016 < 3 30 < 0.05 < < < /10/2017 < 3 37 < 0.05 < < /14/2017 < < < /28/ < 0.05 < < /3/ < <
5 Site 2 Unnamed trib at Bowman Springs Rd CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/28/ < < <2 < /20/2016 <3 612 <0.05 < < < /17/ < < < /13/2016 < < < <3 < /11/ <0.05 < < < /9/2016 < < < < /13/2016 < < < < 2 < /10/2017 < < 0.05 < 0.2 < < /14/2017 < < /28/ < 0.05 < < /3/ < < <
6 Site 3 Village Creek at IH-20 CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/29/ < < /20/ < < /15/ > < /13/ < < /11/ < /9/ < < /14/ < < < /10/ < < < /14/ < /28/ < 0.05 < < < /3/2017 < <
7 Site 4 Village Creek at US-287 BUS CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/28/ < < < /20/ < < < /15/ > < < /13/ < < /11/ < < /9/ < < /13/ < < /10/ < 0.05 < 0.2 < < /14/ < /28/ < 0.05 < < < /3/ < <
8 Site 5 Village Creek near Freeman Dr CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 7/12/ < < /20/2016 < < < < /17/ < < < /13/2016 < < < /11/ < /9/ < < /13/2016 < < < /10/ < 0.05 < 0.2 < < /15/ < < /28/2017 < 3 22 < 0.05 < < < /3/ <
9 Site 6 Village Creek at verman- Kennedale Rd CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/28/ > < < < /20/ <0.05 < <0.02 < < /15/ > < < /13/ <0.05 <0.05 <0.2 < < /10/ < < /9/ < < /13/2016 < < 0.05 < < < /9/2017 < < 0.05 < < /13/ < < < /27/ < 0.05 < < < /4/2017 < <
10 Site 7 Village Creek at Rendon Rd CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/27/2016 < < < < /20/ <0.05 < <0.02 < < /15/ > < < /12/2016 <3 35 <0.05 < < < /10/2016 < < < /8/ < < /12/2016 < 3 24 < 0.05 < < < /9/2017 < < 0.05 < < 2 < /13/2017 < < < < 2 < /27/2017 < 3 22 < 0.05 < < < /4/2017 < < <
11 Site 8 Deer Creek at Oak Grove Rd CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/27/ < <0.02 < < /19/ < <0.02 < < /15/ < < /12/ <0.05 < < < /10/ < < /8/2016 < < < /12/2016 < < < 0.02 < < /9/2017 < < 0.05 < 0.2 < < 2 < /13/2017 < < < < /27/2017 < < < < /4/ < <
12 Site 9 Village Creek at FM 1187 CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/27/ < < < /19/2016 < < < < /15/ > < < /12/ < < /10/2016 < < < /8/ < < /12/2016 < < < /9/2017 < < < 2 < /13/ < /27/ < /4/2017 < < <
13 Site 10 Quil Miller Creek at CR 532 CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/27/2016 < < < /19/2016 < < < /15/2016 <3 > < < /12/2016 <3 64 <0.05 < < /10/2016 <3 200 <0.05 < < /8/2016 < < < /12/2016 < 3 22 < 0.05 < 0.05 < < /9/2017 < 3 49 < 0.05 < 0.05 < < 2 < /13/ < 0.05 < < /27/2017 < 3 17 < 0.05 < /4/ < <
14 Site 11 Village Creek at FM 3391 CHLORHYLL- NITRIT DTCTD (1=YS, 0=NO) (INCHS) (INCHS) 6/27/2016 < < /19/2016 <3 21 <0.05 < < /15/ > < < /12/2016 < <0.05 < < /10/2016 < < /8/ < < /12/2016 < < < 2 < /9/2017 < < < 2 < /13/ < /27/ < < /4/ < <
15 Optical Brighteners Results for data collected: Jun 2016 April 2017 (. coli and Flow plotted on log scale) Potential Sources with positive OB hits High. coli, low flow: malfunctioning septic systems or wastewater infrastructure, greywater High. coli, high flow: large wastewater pipeline break, sanitary sewer overflow Low. coli, varying flows: various chemicals, pesticides, dyes, car washes OB testing is not intended to provide definite results, but instead provide us with another means of identifying possible sources.
16 Correlation Analysis Results for data collected at all sites: Jun 2016 April 2017 Secchi Turbidity Days Since Precip 24 hr rain 72 hr rain Flow NO2 Days Since Precip hr rain hr rain Flow coli * ach of the coefficients in the table below has a p-value of or less; the correlations between each set of parameters is actual and significant. **Arbitrary cutoff of +/- 0.5 was defined to indicate those correlations which may be significant. Significant correlations, Rainfall,, Recent rainfall. coli Recent rainfall,,, Based on this dataset, the correlation coefficients above seem to indicate that constituents such as. coli, nutrients, and solids are being introduced to the watershed primarily through non-point source runoff, and is most likely a non-point source issue.
17 Moving Forward Will submit additional data in Spring 2017 Continue to analyze water quality samples at TRA-CRWS through May 2017 TRA will run statistical and load duration curve analysis using CRWS data Data will be used to guide development of the Village Creek- Lake Arlington WPP
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