Water Quality Monitoring and Parameter Load Estimations in Lake Conway Point Remove Watershed and L’Anguille River Watershed Presented by: Dan DeVun, Equilibrium.

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Presentation transcript:

Water Quality Monitoring and Parameter Load Estimations in Lake Conway Point Remove Watershed and L’Anguille River Watershed Presented by: Dan DeVun, Equilibrium 09/19/2013

Projects Primary Goal By collecting, analyzing and reporting water quality and discharge data; provide monthly and annual parameter loadings, as well as unit area loadings in numerous 12 digit HUCs.

Monitoring Structure – Similar activities are implemented in each monitored watershed that support each project’s primary goal. Water Quality Requirements – Incorporates project design, collection methodology and analytical methodology to generate representative data and allow for an evaluation of water chemistry within the selected watersheds. Discharge Requirements – Estimate the volume of water that passes the monitoring station during the sampling period. Data Compilation and Statistical Analysis – Compile and statistically analyze the collected data to provide monthly, annual, and unit area loadings, as well as, compare results between monitoring stations. Reporting Requirements – Provide the project participants with the project outcomes and make the results readily available to the natural resource and watershed professionals and the general public.

Equilibrium’s Monitoring Requirements Water Quality Sample Types – Discrete grab samples, when possible we collect depth integrated samples at the mid point of the stream Collection Frequency – Once per week (Typically LCPR is collected on Monday and L’Anguille is Thursday) In-situ Parameters – Temperature, dissolved oxygen, specific conductance, pH, and stage. Record Field Notes – documentation that includes type of sample, time and date, site location, name of sampler, climatic characteristics during site visit, recognized problems, and corrective actions required or taken.

Equilibrium’s Monitoring Requirements Water Quality (Continued) Laboratory Parameters – TSS, Turbidity, Total Phosphorus, Total Kjeldahl Nitrogen, Nitrate-Nitrogen, Ammonia-Nitrogen, Total Nitrogen, Chloride and Sulfate. QAQC Samples – Samples taken to insure representativeness of collected data. (include replicate, field blanks, split and spiked samples) Ouachita Water Laboratory – a state certified laboratory, which was established in 1969.

Equilibrium’s Monitoring Requirements Discharge Monitoring Station Location – When possible, locate monitoring stations where existing USGS stations are located. Discharge Parameters – Stage, Profile, and Velocity  Stage – Utilize pressure transducers to continuously measure stage. Additionally, manually measure stage at the time of water quality collection.  Profile – survey and record the stream’s cross sectional profile  Velocity – utilize numerous instruments (electromagnetic and acoustic doppler methodologies) to calculate stream velocities

Equilibrium’s Monitoring Requirements Discharge (Continued) Discharge Measurements – Stream discharge is measured at numerous points throughout the hydrograph. We attempt to measure discharge at a minimal of three different stages of each categorical flow. Low Flow, Mid Flow, High Flow Develop the Stage Rating Discharge Curve – determine the mathematical relationship between stage and discharge for the measured discharge points. Utilize the Stage Rating Discharge Curve – estimate daily discharge from the continuously collected stage data.

Data Compilation and Statistical Analysis Compilation of collected data  Laboratory Water Quality Data  In-situ Water Quality Data  Historical Water Quality Data  QAQC Water Quality Data  Stage Data  Discharge Data  Historical Discharge Data  Precipitation Data Statistical Analysis  Statistical relationship between stage and discharge  Calculation of parameter loadings  Statistical comparison between monitoring stations.

Reporting Provide all project participants with a final report. Provide public access of our data through WQX. Our collected data and analysis can be beneficial to numerous persons working in fields related to water quality and water quantity.

Lake Conway Point Remove Watershed Ten monitoring stations Project Period is July 2011 – October 2014 Monitoring the “outfalls” of 12 digit HUC Currently in data collection phase. LCPR scored 91 in the Final Risk Assessment Matrix Percentile of the Arkansas’ Nonpoint Source Pollution Watershed Risk Matrix and has been selected as a priority watershed. NRCS identified LCPR as a priority in the Mississippi River Basin Healthy Watershed Initiative.

L’Anguille River Watershed Five monitoring stations Previous Project Period July 2011 – June 2012 Current Project Period July 2012 – September 2015 Monitoring the “outfalls” of 12 digit HUC The L'Anguille River was included on the Arkansas (d) list for not supporting aquatic life due to siltation/turbidity and has been on each subsequent 303(d) list. ANRC has designated the watershed as a priority watershed. NRCS also identified the L'Anguille River as a priority in the Mississippi River Basin Healthy Watershed Initiative.

Priority Ranking by SWAT Model 12-Digit HUC Name Drainage Size (Acres) Sediment Load (Percentile) Total Phosphorus Load (Percentile) Erosion Rate Cartographic Score Copper Creek 12, Critical Prairie Creek 11, Critical Indian Creek 21, ModerateCritical Upper Brushy Creek 21, Slight Middle Brushy Creek 31, Slight Saraswat, et.al

2011 – 2012 Hydrographs

2011 – 2012 Results Computed Annual Loading StationCubic Feet per Year TPTKNAmmoniaTSSNO 3 -NChlorideSulfateTN LBS/Year UB 2,350,000,00053,700167,00011,40011,100,00013,6002,480,0001,500,000181,000 MB 4,120,000,000117,000345,00020,30028,300,00035,8003,830,0003,220,000381,000 CC 1,060,000, 00020,60062,2006,6806,840,00020,100419,000699,00082,300 PC 1,170,000, 00040,40061,4002,77021,100,00013,200323,000583,00074,600 IC 2,850,000, 00085,900226,00021,00021,000,00055,8001,570,0002,140,000282,000

2011 – 2012 Results Unit Area Loading UBMBCCPCIC Acres21,71831,94712,05611,62621,034 LB/Acre TP TKN Ammonia TSS ,8181,001 NO 3 -N Chloride Sulfate TN

0-20% 20-40% 40-60% % Sediment Contribution Swat Model Percentile Contribution

40-60% 0-20% 60-80% Total Phosphorus Contribution Swat Model Percentile Contribution

Project Difficulties Variable Climatic Patterns Stream Activities Unnatural Discharges Equipment loss Discharge Measurements