removal and restoration of in-stream sediment ponds: part

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Removal and Restoration of In stream Removal and Restoration of Instream Sediment Ponds: Part 1 – Sediment Pond Removal and Enhanced Designs Removal and Enhanced Designs Appalachian Stream Mitigation Workshop Workshop Lexington, Kentucky April 11 15 2011 April 1115, 2011 Richard C. Warner Ui it fK t k UniversityofK entucky

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Page 1: Removal and Restoration of In-stream Sediment Ponds: Part

Removal and Restoration of In streamRemoval and Restoration of In‐stream Sediment Ponds: Part 1 – Sediment Pond 

Removal and Enhanced DesignsRemoval and Enhanced Designs

Appalachian Stream Mitigation WorkshopWorkshop

Lexington, KentuckyApril 11 15 2011April 11‐15, 2011 

Richard C. WarnerU i it f K t kUniversity of Kentucky

Page 2: Removal and Restoration of In-stream Sediment Ponds: Part

OverviewOverview

• Sediment pond removal considerationsSediment pond removal considerations– Current Methods

• Designing sediment ponds to• Designing sediment ponds to– Cost‐effectively remove/control deposited sedimentsediment

– Reduce potential environmental impacts

R t t t– Reconstruct streams

• Enhanced sediment control

Page 3: Removal and Restoration of In-stream Sediment Ponds: Part

Sediment Pond Removal dConsiderations

• SchedulingScheduling• Baseflow diversion• Dewatering provisions• Dewatering provisions• Sediment handlingP t ti l t di h di t• Potential to discharge sediment

• Down‐gradient sediment control(s)• Erosion control(s)• Stream reconstruction• Riparian vegetation

Page 4: Removal and Restoration of In-stream Sediment Ponds: Part

SchedulingScheduling

• Low storm probabilityLow storm probability– Lowest monthly rainfall ‐ September through and NovemberNovember

• High evapotranspiration timeframeHighest evapotranspiration June through August– Highest evapotranspiration – June through August 

• Low base flow timeframe– Largest difference between rainfall and evapotranspiration – June through September

Page 5: Removal and Restoration of In-stream Sediment Ponds: Part

BaseflowBaseflow

• Almost all sediment ponds had baseflowAlmost all sediment ponds had baseflow emanating year‐round from a valley fill

Page 6: Removal and Restoration of In-stream Sediment Ponds: Part

Observed Baseflow Diversion MethodsObserved Baseflow Diversion Methods

• Baseflow diversion options usedBaseflow diversion options used– Small dam built up‐stream and pump to pipeline to bypass baseflowto bypass baseflow

– Diversion built to bypass baseflow

– Temporary diversion constructed and ‘stabilized’– Temporary diversion constructed and  stabilized  within sediment pond 

– No baseflow diversion provisionsNo baseflow diversion provisions

Page 7: Removal and Restoration of In-stream Sediment Ponds: Part

Sediment PondsSediment Ponds

• LocationLocation– Near toe of valley fill

– Further down‐gradient of valley fillg y

• Type of spillways– Single spillway (emergency spillway design)Single spillway (emergency spillway design)

– Emergency spillway with straight‐pipe

– Emergency spillway with drop inlet

– Emergency spillway with perforated riser

• Disadvantage – wet deposited sedimentg p

Page 8: Removal and Restoration of In-stream Sediment Ponds: Part

Dewatering MethodsDewatering Methods

• Predominantly pump over emergency spillwayPredominantly pump over emergency spillway or through principal spillway

• Sump(s) used to further reduce water level• Sump(s) used to further reduce water level

• Trench occasionally used to reduce water level

• Siphons occasionally used in lieu of pump

• Incrementally remove embankmenty

Page 9: Removal and Restoration of In-stream Sediment Ponds: Part

Sediment Handling OptionsSediment Handling Options

• Difficult and costly to remove and transportDifficult and costly to remove and transport sediment that has been dewatered by previously listed methods– Long arm backhoe used but low‐production rate

• Sediment wave – push deposited sediment with materials removed from the embankment

• Sediment blending – blend embankment materials with deposited sediment (can only be accomplished when deposited sediment is relatively dry)

Page 10: Removal and Restoration of In-stream Sediment Ponds: Part

High Potential to Discharge SedimentHigh Potential to Discharge Sediment

• Poor scheduling timeframePoor scheduling timeframe

• High baseflow

ll d b f b fl• No controlled bypass of baseflow

• Sediment ponds without dewatering options– Inadequately dewatered sediment

Page 11: Removal and Restoration of In-stream Sediment Ponds: Part

Down‐gradient Sediment ControlsDown gradient Sediment Controls

• Often time ‐ none usedOften time  none used

• ControlsSt b l– Straw bales

– Rock check dam located in stream

Page 12: Removal and Restoration of In-stream Sediment Ponds: Part

Erosion Control of Stream Bank and Riparian Zone

• Often time none usedOften time none used

• ProductsSt l h– Straw mulch

– Excelsior blankets (infrequently used)

– Grasses and legumes

Page 13: Removal and Restoration of In-stream Sediment Ponds: Part

Sediment Pond Designs for Efficient d d b k lSediment and Embankment Removal

• Valley fill designValley fill design

• Passive/active dewatering provisions

l i h b d i• Multi‐chamber design

Page 14: Removal and Restoration of In-stream Sediment Ponds: Part

Valley Fill DesignValley Fill Design

• Sediment ponds built down‐gradient of valleySediment ponds built down gradient of valley fills constructed with new specific‐conductivity minimization techniques had noconductivity minimization techniques had no baseflow between mid‐May and mid‐NovemberNovember

• Hence, sediment pond removal should occur in October and November when the chance ofin October and November when the chance of a storm event is minimal

Page 15: Removal and Restoration of In-stream Sediment Ponds: Part

Sediment Pond Dewatering Design Options

• Floating siphon• Floating decant• Internal sand‐gravel filterE t l d l filt• External sand‐gravel filter

• Advantages:– Drier sediment – much more cost effective removal or soil blending with embankment

– Slightly higher deposited sediment density– Enhanced stream channel stabilizationEnhanced stream channel stabilization– Greater opportunity for tree establishment in riparian zone

Page 16: Removal and Restoration of In-stream Sediment Ponds: Part

Floating SiphonFloating Siphon

Page 17: Removal and Restoration of In-stream Sediment Ponds: Part

Sand-Gravel FilterConstruction Alternatives

Pond BedGravel

Pond Bed

CleanSand

G lGravel

Geotextile

Page 18: Removal and Restoration of In-stream Sediment Ponds: Part

Internal Sand‐gravel FilterInternal Sand gravel Filter

Page 19: Removal and Restoration of In-stream Sediment Ponds: Part

External Sand‐gravel FilterExternal Sand gravel Filter

Page 20: Removal and Restoration of In-stream Sediment Ponds: Part

Multi‐chamber designMulti chamber design

• Use slope for passive dewatering to down‐Use slope for passive dewatering to downgradient chamber

• Size up gradient chamber for efficient• Size up‐gradient chamber for efficient sediment removal

Si i b f k• Size separation berm for excavator – truck operation

Page 21: Removal and Restoration of In-stream Sediment Ponds: Part

Multi‐chamber Sediment PondMulti chamber Sediment Pond

Page 22: Removal and Restoration of In-stream Sediment Ponds: Part

Multi‐chamber PondMulti chamber Pond

Page 23: Removal and Restoration of In-stream Sediment Ponds: Part

Multi‐chamber PondMulti chamber Pond

Page 24: Removal and Restoration of In-stream Sediment Ponds: Part

Sediment ControlSediment Control

• Combination weep berm – natural grass filterCombination weep berm  natural grass filter

• AdvantagesAll f i filt ti ll di t ti d– Allows for infiltration as well as sedimentation and sediment storage

Directs overflow slowly into natural riparian zone– Directs overflow slowly into natural riparian zone or grass filter for further treatment

Sediment trap efficiency ~ 99+%– Sediment trap efficiency   99+%

Page 25: Removal and Restoration of In-stream Sediment Ponds: Part

Weep BermWeep Berm