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Calculations and Methodology - Semcog

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<strong>Calculations</strong> <strong>and</strong> <strong>Methodology</strong><br />

Scott Dierks<br />

JFNew


<strong>Calculations</strong> & <strong>Methodology</strong><br />

• Chapter 9 LID manual<br />

• Describes design methods to calculate<br />

LID techniques<br />

– Mimicking presettlement hydrology<br />

• Presettlement vs. Predevelopment


Implementing a Community<br />

Stormwater Regulation<br />

• Discuss & decide on water quality<br />

outcomes<br />

• Adopt design st<strong>and</strong>ards that achieve<br />

desired outcomes<br />

• Select stormwater methodologies to<br />

meet the design st<strong>and</strong>ards


NPDES Phase II New Stormwater<br />

Permit Requirements (rule issued<br />

May 22, 2008)<br />

• Create/enforce regulation of post-construction<br />

runoff for new <strong>and</strong> redeveloped projects >1 acre<br />

– Minimum treatment volume – one inch of runoff or<br />

runoff from 90% exceedance event<br />

– Projects must demonstrate minimum 80% TSS<br />

removal <strong>and</strong> no more than 80 mg/L leaving site<br />

– Post construction peak <strong>and</strong> total runoff = preconstruction<br />

(channel protection criteria)


LID Design Criteria<br />

• Groundwater recharge<br />

• Channel protection<br />

• Prevention of downstream flooding<br />

• Water quality protection<br />

• Evapotranspiration & the natural<br />

hydrologic/water cycle


Channel Protection Criteria<br />

• Bankfull condition responsible for<br />

shaping of channel<br />

• Match post construction runoff volume<br />

<strong>and</strong> rate to presettlement conditions up<br />

to bankfull


Channel Protection Criteria<br />

• LID site design based on no increase of<br />

presettlement runoff condition for all<br />

storms up to the 2-year, 24-hr return<br />

frequency<br />

– 95% of annual rainfall volume


Rainfall Distribution by Storm<br />

Lansing, Michigan


Waivers to Channel<br />

Protection Criteria<br />

• Waivers for certain site constraints<br />

– Poor draining soils, contaminated soils,<br />

bedrock, high water table, karst geology<br />

• Identify alternative st<strong>and</strong>ards<br />

– Detention of 1 yr, 24 hour storm <strong>and</strong> water<br />

quality criteria<br />

• Model ordinance


Flood Protection Criteria<br />

• Flood control based on local needs<br />

& flood risk<br />

• Volume runoff is maintained at<br />

presettlement value, peak rate will also be<br />

maintained up to the same storm.<br />

• Flood protection beyond presettlement<br />

value, additional control may be needed.


Flood Protection Criteria<br />

• Maintain presettlement runoff volume<br />

<strong>and</strong> rate for storms up to 2 year event.<br />

• Maintain the presettlement peak runoff<br />

rate for all storms up to the 100 year<br />

event or that determined by local<br />

st<strong>and</strong>ard.


Additional Flood Control<br />

• Many use 100 year storm<br />

• Fixed release rate<br />

• Exemptions for issues small sites or<br />

direct discharge to certain waterbodies<br />

• Model ordinance


Groundwater Recharge Criteria<br />

• Essential for providing stream flows <strong>and</strong><br />

groundwater supplies<br />

• Implement a volume control criteria <strong>and</strong><br />

maximize use of infiltration BMPs


Water Quality Criteria<br />

• Bacteria from wildlife<br />

• Nutrients from excessive fertilizer<br />

• Suspended solids from eroded<br />

streambanks, roads, & construction sites<br />

• Hydrocarbons <strong>and</strong> trace metals<br />

• Chlorides from road salt


Water Quality Criteria<br />

• Quantitative goal = 80% reduction in<br />

Total Suspended Solids based on postdevelopment<br />

l<strong>and</strong> use<br />

• Meet channel protection volume, meet<br />

water quality volume


Water Quality Criteria<br />

• Options for treatment volume<br />

– 0.5 inch of runoff<br />

– 1 inch of runoff from impervious areas &<br />

0.25 inches from disturbed pervious areas<br />

– 1 inch of runoff from disturbed pervious &<br />

impervious areas<br />

– 90% of runoff producing storms


Other Water Quality Issues<br />

• Soluble pollutants<br />

• Hot spot & high risk areas<br />

Stormwater Hot Spots<br />

Vehicle Maintenance <strong>and</strong> Repair Facilities<br />

Vehicle Fueling Stations<br />

"Fast Food" Restaurants<br />

Convenience Stores<br />

Outdoor Chemical Mixing or H<strong>and</strong>ling<br />

Outdoor Storage of Liquids<br />

Commercial Nursery Operations<br />

Other Uses or Activities Designated by Appropriate Authority<br />

Minimum Pre-Treatment Options<br />

A, E, F, G<br />

A, D, G<br />

B, C, D, I, K<br />

B, C, D, I, K<br />

G, H<br />

G<br />

I, J, L<br />

As Required


Evapotranspiration<br />

• ET is largest component of the<br />

hydrologic regime<br />

• Difficult to quantify<br />

• Minimize loss by protecting existing<br />

vegetated areas & replacing vegetation<br />

lost or removed.


Nonstructural BMPs<br />

• Protected presettlement areas are subtracted<br />

from site development for purposes of<br />

designing LID-based treatments.<br />

– Protect sensitive areas<br />

– Protect riparian buffers


Stormwater Credits<br />

• Reduces volume of runoff<br />

• Enhance the response of a piece of l<strong>and</strong><br />

to a storm event rather than treat the<br />

runoff that is generated<br />

• Based on the Curve Number method of<br />

analysis


Stormwater Credits<br />

• Credited BMPs<br />

– Minimize soil compaction<br />

– Protection of existing trees<br />

– Soil restoration<br />

– Native revegetation<br />

– Riparian buffer restoration


Example Stormwater Credits<br />

• Native revegetation/Riparian buffer<br />

restoration<br />

• Proposed trees <strong>and</strong> shrubs to be planted under the<br />

requirements of these BMPs can be assigned a<br />

Curve Number (CN) reflecting a woods in "good"<br />

condition for an area of 200 square feet per tree or<br />

the estimated tree canopy, whichever is greater. For<br />

shrubs, an area of 25 square feet per shrub.


Calculating Runoff<br />

• Runoff volume<br />

• Peak rate<br />

• Runoff Hydrograph


Runoff Volume Calculation<br />

• Various methods available<br />

– Runoff Curve Number (CN) method


Peak Rate /<br />

Hydrograph Estimations<br />

• NRCS (SCS) Unit Hydrograph Method<br />

• Modified Unit Hydrograph Method for<br />

Michigan<br />

• The Rational Method


Computer Models for<br />

Calculating Runoff<br />

• HEC Hydrologic Modeling System (HEC-<br />

HMS)<br />

• SCS/NRCS Models: WinTR-20 & WinTR-55<br />

• Stormwater Management Model (SWMM)<br />

• Source Loading <strong>and</strong> Management Model<br />

(SLAMM)<br />

• Continuous Modeling


Calculating Peak Rate By<br />

Utilizing Volume Control<br />

• Volume reduction BMPs <strong>and</strong> LID<br />

practices reduces or eliminates storage<br />

required for peak rate<br />

• Difficult to quantify peak rate benefits<br />

of LID<br />

• Milwaukee Metropolitan Sewerage District<br />

“Quicksheets”<br />

• Various other resources noted in manual


Precipitation Data<br />

• Rainfall Frequency Atlas of the Midwest<br />

– www.sws.uiuc.edu/pubdoc/B/ISWSB-<br />

71.pdf<br />

• United States Historical Climatology<br />

Network<br />

– http://cdiac.ornl.gov/epubs/ndp/ushcn/state<br />

_MI.html


Design Calculation Process<br />

Step 1: Provide general site information<br />

Step 2: Map the existing features of the site<br />

Step 3: Layout the proposed development<br />

avoiding protected areas


Design Calculation Process<br />

Step 4: Determining the disturbed area size<br />

Step 5: Calculate the level of volume control<br />

needed for channel protection


Design Calculation Process<br />

Step 6: Select volume control BMPs<br />

Step 7: Peak rate exemption for small sites<br />

Step 8: Calculate peak rate control<br />

Step 9: Determine water quality volume &<br />

select BMPs (If needed)


Step 1:<br />

Provide<br />

General Site<br />

Information


Step 2:<br />

Map<br />

Existing<br />

Features


Step 3: Layout Proposed<br />

Development<br />

• If after development is sited, addition<br />

sensitive areas are impacted, modify<br />

worksheet 2.


Step 4:<br />

Determine<br />

Disturbed<br />

Area Size


Step 5:<br />

Calculate<br />

volume<br />

control<br />

needed for<br />

channel<br />

protection


Step 6:<br />

Select<br />

volume<br />

control<br />

BMPs


Step 7:<br />

Peak Rate<br />

Exemption<br />

for Small<br />

Sites


Step 8:<br />

Calculate<br />

Peak Rate<br />

Control


Step 9:<br />

Determine<br />

Water<br />

Quality<br />

Volume<br />

(if needed)


Example for Calculating LID<br />

BMP Peak Rate Benefits<br />

• Milwaukee Metropolitan Sewage District LID<br />

“Quicksheet” (See:<br />

http://v2.mmsd.com/Assets/Documents/stormwaterweb/<br />

PDFs/Appendix_L.pdf)<br />

• Total site retention (sum of distributed BMP retention)<br />

is set as uniform depth of storage across the site<br />

• Runoff “occurs” only after runoff depth >uniform<br />

storage depth


<strong>Calculations</strong> <strong>and</strong> <strong>Methodology</strong><br />

Scott Dierks<br />

JFNew

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