HomeMy WebLinkAboutNC0063096_Meeting Notes_20080821NPDES DOCUNENT SCANNING COVER SHEET
NPDES Permit:
NC0063096
Holly Springs WWTP
Document Type:
Permit Issuance
Wasteload Allocation
Authorization to Construct (AtC)
Permit Modification
Complete File - Historical
Engineering Alternatives (EAA)
Correspondence
Owner Name Change
Meeting Notes
Instream Assessment (67b)
Speculative Limits
Environmental Assessment (EA)
Document Date:
August 21, 2008
Vies docurnerit is printed on reuse paper - igm.ore any
content on tine reYerese'side
Meeting to Discuss Harris Lake
Modeling and Monitoring
August 21, 2008 @ 2:30-4:00 PM
Archdale Building,14th Floor, Conference Room No. 3
1. Introduction and Purpose of the Meeting
2. Model development process
3. Overview of model calibration
4. Preliminary results of discharge sensitivity
5. Information to present to EMC Water Allocation Committee in September
6. Discussion/Next Steps
Modeling Review Meeting
Western Wake Regional Wastewater
Management Facilities
Harris Lake Model Update
lu;ust 21, 200$
Review Topics
♦ Model development process
♦ Calibration Status
♦ Preliminary results for discharge
sensitivity
♦ Information to present EMC Water
Allocation Committee in September
♦ Discussion/Next Steps
Review Topics
♦ Model development process
♦ Calibration Status
♦ Preliminary results for discharge
sensitivity
♦ Information to present EMC Water
Allocation Committee in September
♦ Discussion/Next Steps
1
Overall Modeling Process
• Modeling approach- Complete
• Modification of monitoring program - Complete
• Development of watershed and lake models - Complete
• Screening with BathTuh model — Complete
• Model Calibration - 2ntl Draft Complete
• Draft TM submitted — DWQ review meeting August 11
• Comments received on August 19
• Model Sensitivity to Discharge - July -August 08
• Preliminary model report - August -Sep 08
• EMC Update on Harris Lake - Sep 08
• 2008 Monitoring data available - Nov 08
• Updated model analyses and reports - Jan 09
Model Development
• Preliminary Scenario Analysis based on BatliTub
• Watershed Model
• Adapted Utley Creek Generalized Watershed
Loading Function (GWLF) model to estimate
nonpoint source loading to Harris Lake
• CE-DUAL-W2 Model of the Lake
• Based on Jan. 08 detailed bathymetric data
• Divided lake into segments with similar
characteristics
• Processed GWLF and point source nutrient
loadings for the period from 2001 - 2007
• Doveloped meteorological inputs based local
Progross data
2
Review Topics
• Model development process
• Calibration Status
• Preliminary results for discharge
sensitivity
• Information to present EMC Water
Allocation Committee in September
• Discussion/Next Steps
Se16 /{(
PisU f-
3
Lake Model Calibration Steps
• Check flow balance
• Calibrate temperature to profiles
• Evaluate balance of organic and
inorganic nitrogen species (TKN, NH4,
NO3)
• Calibrate total nitrogen and total
phosphorus
• Calibrate chlorophyll a
• Calibrate dissolved oxygen to profiles
Calibration Status
• Preliminary Calibration Completed
• Based on Quarterly data at 4 stations
- Used 2006 for calibration 8 2007 for verification
Examined predictions versus results for 2002 through
2007
• Draft TM submitted to Partners and DWQ
• Review meeting held on August 11
• Comments received on August 19
• Next Steps
• Address comments
• Complete preliminary discharge sensitivity analysis
• Update model based on 2008 monitoring
- 2 additional stations
- Increased collection frequency
Harris Lake Monitoring Locations
'r�- tticv 5 i nv ro
4
Calibration Observations
• NPS Nitrogen species are underestimated
• Not critical because TN/TP ratios high
• Focused on NPS TP
• Temperature and DO predictions are generally
very good
• Chlorophyll a simulation captures range and
expected pattern of algal growth
• Underestimates levels during non -growing
season
• Can be refined using temperature parameters
Review Topics
• Model development process
• Calibration Status
• Preliminary results for discharge
sensitivity
• Information to present EMC Water
Allocation Committee in September
• Discussion/Next Steps
Evaluation of Potential Scenarios
• Baseline - existing conditions
• Phase 1 - Initial WRF discharge
• 220' lake elevation
• Western Wake WRF discharge rate of 18 mgd
• HS discharge rate of G mgd
• Existing Landuse
• Combined discharge and separate discharge
• Phase 2 - Long term WRF discharge
• 220' and 240' lake elevation
• WRF discharge rate of 30 mgd
• HS discharge rate of 8 mgd
• Future Landuse with BMPs
5
Comparison of chlorophyll a concentrations above the Main Dam a? 220'
Baseline and 24 mgd at 2 mg1L TP
Comparison of WRF $c.nYba
al la mad
■ICI i','1■Irl I.
Comparison of chlorophyll a concentrations above the Main Dam E; 220'
Baseline and 24 mgd at 2 & 0.5 mg/L TP
Commie. of WRF MonWpa
M 7A mei
Comparison of chlorophyll a concentrations above the Main Dam @ 220'
Baseline and 24 mgd at 2, 0.5, & 0.25 mg/L TP
CanpeYena1WRF Scenario*
at 24 aqd
—WNW—+..••.f.
—.aM•a. n'—..w..n'
•
■•1I■11M111111•41■IY1',11
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■■I■EMIIIIIMS j.111111M1
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ni
riletf,loy - (4-
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bkit
6
Comparison of chlorophyll a concentrations above the Main Dam `d 220'
Baseline and24 mgd at 2, 0.5, 0.25, & 0,1 mg/L TP
Comparison of chlorophyll a concentrations at discharge location « 220'
Baseline and,24 mgd at 2, 0.5, 0.25, & 0.1 mg/L TP
0V'—awM.vv
Comparison of chlorophyll a Concentrations in Utley Creek
Combined Discharge vs Separate WRF and Holly Springs Discharge
5U
w
m
Co..,Mn. OW. a..
WPM On„ar,m
— :a.ca oossr>
— ,a.s.@oasrw,e
- uow
E. ,111=111MIIN
10
b. (
,tti (d62.
7
Dynamic Simulation of Chlorophyll a
24 mgd Combined Discharge at 2 mg/L TP
MI 140.261•
i'
i
Dynamic Simulation of Chlorophyll a
18 mgd WW Discharge Plus 6 mgd Holly Springs at 2 mgiL TP
Comparison of Current and Future Landuse
Baseline Results at the Main Dam
Comparison of Existing and Foto .
Bastogne NI •
— Cupp
— ru..erpp,e,n
8
Comparison of Current and Future Landuse
Baseline Results in the Utley Creek Arm
Lerrplemd 6f10y.116n �J+Rrb
IYrygrW Ann
Eislrp
— f RanroW BAN
— rJn ennenowtsH
t
5 as
•
f u
w
II I,rl1 . IT= All 'W I I
it
Comparison of chlorophyll a concentrations above the Main Dam rah 220'
Baseline and 38 mgd at 2. 0.5, 0.25, & 0.1 mg/L TP
Comparison of chlorophyll a concentrations at Discharge Location @ 220'
Baseline and 38 mgd at 2, 0.5, 0.25, & 0.1 mg/L TP
9
Comparison of chlorophyll a concentrations at 220' and 240' Elevation
Above the Main Dam
Baseline and, 38 mgd discharge @ 0.25 mg/L TP
Comparison of la mad WRr wnvIo.
n 220' an xis' LY. L.v.l
240' Lake Level Caveats
• Current 240' Lake Level Run Assumptions
• Future urban landuse meets Jordan Lake rules for TP
- Stormwator controls on new development
- Prirnadly impacts high densely development and commerclil
landusos
- Reduces NPS TP loading by approximately 10%
• No assumption for Increase In cooling water discharge
volume
- Expansion of the nuclear plant would Include a higher
discharge volume
- Plant currently uses polyorlhophosphato for anticorrosion
measures
• No additional changes in water balance
- Minimum release from darn not Included
- Pumping from Cape Fear River not Included
Prelijninary Conclusions from
Scenarios
• Exceedances of chlorophyll a standard likely
at discharge TP concentrations above 0.25
mg!L
• Removal of Holly Springs WWTP from Utley
Creek provides little benefit to Harris Lake
• Model includes TP removal in Thomas
Millpond
10
Preliminary Conclusions
(Continued)
♦ Increase to 38 mgd has minimal impact at the
0.25 mg/L TP level
• Increased flushing and reduced residence time
outweighs higher TP load
♦ Higher lake level (240 elevation) provides
significant buffering capacity
• Scenario assumes NPS controls and no
increase in TP from cooling water
Review Topics
♦ Model development process
♦ Calibration Status
♦ Preliminary results for discharge
sensitivity
♦ Information to present EMC Water
Allocation Committee in September
♦ Discussion/Next Steps
Topics for EMC Discussion
♦ Status of modeling
• Brief highlights of earlier slides
• Preliminary sensitivity
• Schedule
♦ Potential IBT related issues
• Downstream concerns (moving
discharge from CF River)
• Impacts on WRF Schedule
11
Comparison of Discharge from the Harris Lake Main Dam
under sting and WRF Scenarios
Sao
453
403
350
303
353
1m
IEo
Com y.rlon of M.In D. m e1rhmIgo
— Etlbp oWwlal
— 14 5030S lal
—Hmpe PYe.lal
— 34 0I25..3104w1
Iii -'_
•iimulmium
AmtRwitil=N ■;t"m
MiWitANtigaii Mlle=
as Lake Outflow Predictions
Flow Existing
Information Outflow
Aluage Flow
for 2001•
2007 - ds
I019d1 32.0 (20.6]
Average
Summer
Flow for
2001.2007 -
ds (nrgdJ 12.7 (8.2]
Median Summer
Flow for
2001-2007 -
ds (mgd) 1.4 (0.9]
Total Days
below 7010
[2001.2007) 406
I'.... r. r 1. .. ..l
Outflow with
24 mgd
WRF
68.6 (43.0]
35.9123.1]
26.8 (17.3]
45
Outflow with
38 mgd
WRF
87.2 [56.3)
55.0[35.51
46.2 (29.81
Outflow with
38 mgd
WRF - 240'
75.3148.61
34.4 (22.2]
29.0 (18.7)
0
Review Topics
• Model development process
• Calibration Status
• Preliminary results For discharge
sensitivity
• Information to present EMC Water
Allocation Committee in September
• Discussion/Next Steps
12