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Merritt's Presentation

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Project Investigators Robert Walter, Franklin & Marshall College Dorothy Merritts, Franklin & Marshall College Michael Rahnis, Franklin & Marshall College Michael Langland, Dan Galeone, and Allan Gellis, US Geological Survey William Hilgartner, The Johns Hopkins University David Bowne, Elizabethtown College John Wallace, Millersville University PA Fish and Boat Commission Paul Mayer, Ken Forshay, Roxanne Adeuya, and Bart Falkner, EPA Funders PA DEP (Jeff Hartranft), US EPA, F&M NSF grants Engineers LandStudies, Inc. Evalua&ng a New Approach to Aqua&c Resource Restora&on, Big Spring Run, PA
Transcript

     

Project  Investigators      

 Robert  Walter,  Franklin  &  Marshall  College  Dorothy  Merritts,  Franklin  &  Marshall  College  Michael  Rahnis,  Franklin  &  Marshall  College  

Michael  Langland,  Dan  Galeone,  and  Allan  Gellis,  US  Geological  Survey  William  Hilgartner,  The  Johns  Hopkins  University  

David  Bowne,  Elizabethtown  College  John  Wallace,  Millersville  University  

PA  Fish  and  Boat  Commission  Paul  Mayer,  Ken  Forshay,  Roxanne  Adeuya,  and  Bart  Falkner,  EPA  

 Funders  

PA  DEP  (Jeff  Hartranft),  US  EPA,  F&M  NSF  grants    

 Engineers  

LandStudies,  Inc.  

Evalua&ng  a  New  Approach  to  Aqua&c  Resource  Restora&on,  Big  Spring  Run,  PA  

     Lauren   Manion   ‘04,   Graham   Boardman   ‘05,   Serena  Wren,   ‘05,   Christina   Arlt   ’05,  Caitlin  Lippincott  ‘05,  Sauleh  Siddiqui  ‘07,  Yoanna  Voynova  ‘06,  Andrey  Voynov  ‘05,    A.  Sullivan  ‘06,  Adam  Ross  ‘07,  Mark  Voli  ‘08,  Chris  Scheid  ‘08,  Zach  Stein  ‘08,  Julie  Weitzmann   ‘08,   Colette  Buchanan   ’08,  Doug  Smith,   ‘08,  Alison  Winterer,   ‘09,   Zain  Rehman   ‘09,   Brian   Hughes,   ‘09,   Erik   Ohlson   ‘10,   Franklin   Dekker   ‘10,   Stacey  Sosenko  ‘09,  Liz  Cranmer  ‘09,  Matt  Jenschke  ’09,  Wanlin  Deng  ‘12,  Katie  Datin  ‘12,  Laura   Kratz   ’11,   Andrea   Shilling,   ‘10,   Yupu   Zhao,   ’10,   Derek   Matuszewski,   ‘10,  Austin   Reed,   ‘10,   Alex   DiIonno,   ‘10,   Erik   Olsen,   ‘11,   Ali   Neugebauer,   ’11,   Elvis  Andino,   ‘12,   Peter  Rippberger,   ‘12,  Aakash  Ahamed,   ‘12,   Conor  Neal,   ’12,  Danielle  Verna  ,  ‘12,  Joe  Galela,  ’11.,  Kayla  Schulte,  ‘13,  Aaron  Blair  (IUP),  ‘13,  Evan  Lewis,  ‘15      

Evalua&ng  a  New  Approach  to  Aqua&c  Resource  Restora&on,  Big  Spring  Run,  PA  

Student  Collaborators    

Landowners    

 J.  Sweeney,  Kirchner  Family,  and  H.  Keener  (Big  Spring  Run)  

Note:    All  videos  in  this  ppt  can  be  seen  at    

h3p://www.youtube.com/channel/UCorgwKIsH03jLRuTSF3Wxzg  

 •  Piedmont  stream  

 •  South  of  Pleistocene    

glacial  ice  margin    

•  Pleistocene  permafrost    

•  Silt  belt  (loess)    

•  Predominantly  agriculture  historically    

•  Wheat  belt    

•  Limestone  bedrock    

Big  Spring  Run,  PA  

BRID

GE

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ROSIER WAYCHELSEA LOOP

NEWPORT

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SPRECHER RD

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CEDAR DRBIRCH DR

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KINDER AVE

CASEY DR

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DONNELLY DR

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VIOLET AVE

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EAGLE DRBALD

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MIL LW

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BEAVER VALLEY PIKE

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76°13'0"W

76°13'0"W

76°14'0"W

76°14'0"W

76°15'0"W

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76°16'0"W

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76°17'0"W40°0'0"N

40°0'0"N

39°59'0"N

39°59'0"N

I0 1,000 2,000 3,000 4,000 ft

Big Spring Run Watershed

Big  Spring  Run  Watershed,  PA  (~15  km2)  

Big  Spring  Run  Restora&on  Reach  

04/2005

04/2013

Pre-­‐Restoration  

Post-­‐  Restoration  

 •  Buried  wetland  landscape—ecosystem  

values  can  be  rejuvenated  

•  Modern  incised  stream  

•  Modern  high  loads  of  bank  erosion  and  suspended  sediment  in  stream      

•  High  nutrients  in  surface/groundwater    

•  Limited  habitat,  invasive  species    

•  303d  listed  stream  

Why  Restore  It?  

Big  Spring  Run:      Typical  Incised  mid-­‐Atlan&c  Stream  

 

Flume  experiments  and  video  footage  from  Dr.  Allesandro  Cantelli,  Univ.  of  Minnesota,  NCED    h\p://www.nced.umn.edu/Stream_Restora&on_Toolbox.html  

~80  yr  old  channel  

Exhumed  Pleistocene  

Gravel  

300-­‐yr  old  wet  meadow  

Dam  removal  and  breaching:    Incision  and  bank  erosion,    exposing  buried  landscape      

Pompeii  Effect  

1  hr  40  minutes  old  

Big  Spring  Run:      Typical  Incised  Mid-­‐Atlan&c  Stream  

 

Flume  experiments  and  video  footage    Dr.  Allesandro  Cantelli,    University  of  Minnesota    h\p://www.nced.umn.edu/Stream_Restora&on_Toolbox.html  

Exhumed  Pleistocene  

Gravel  

Dam  removal  and  breaching:    Incision  and  bank  erosion,    exposing  buried  landscape      

Wetlands  and  Their  Value  

       Ecosystem  services    they  provide:  –  Habitat  for  fish  and  wildlife  

–  Improved  water  quality  –  Storing  floodwaters  – Maintaining  surface  water  flow  

–  DenitrificaSon    

Objec&ve:  Rejuvenate  the  ecological  funcSon  of  the  buried  wetland.    

Banta Restoration (2004) on Lititz Run, Warwick Twp., Lancaster Co., PA

•  90  tons/yr  silt  from  ~3000  e  of  stream  bank  erosion  

 •  Majority  of  erosion  in  winter  (Dec-­‐Mar)    

•  Majority  of  suspended  sediment  transport  in  April,  May,  December  

•  Associated  nutrients  

Why  Restore  It?  

New  Freeze-­‐thaw  Apron  Forming  8  Days  aeer    Jan  25,  2010,  High  Flow  Event,  Big  Spring  Run,  PA  

Yellow  arrows  mark  trim  line  from  high  water  event  

Needle  ice  and    bank  erosion,  SE  PA  

0                            2  cm  

Needle  Ice  Forma&on  and  Erosion  on  Stream  Bank,  Big  Spring  Run,  PA  Day  and  Night  (Infrared)  Field  Camera,  March-­‐April  2011  

Thesis  work  of  J.  Galella,  2010-­‐11,  F&M  College  

Restore  to  What?  

From:  Findlay  and  Taylor,  2006,  Why  rehabilitate  urban  river  systems?  ,  Area,  v.  38,  p.  312-­‐325.  (Modified  from  Rutherfurd  et  al,  2000.)  

#  sides  signifies  SYSTEM  complexity  and  biodiversity  

Ecosystem  structure  or  species  richness  

Ecosystem  fu

nc&o

n  or  biomass    

(#  individu

als,  indica&o

n  of  produ

c&vity)  

Original  Ecosystem  

Partly  Re-­‐instated  Ecosystem  

Degraded  Ecosystem  

Created/Modified  Ecosystem  

Remedia4on  

Degrada4on  

Holocene  Streams  in  Low-­‐Relief  Landscapes  

Although  anabranching  channels  are  considered  relaSvely  uncommon  today,  a  review  of  archaeological,  historic  and  geomorphological  evidence  indicated  that  anastomosing  channels  and  floodplain  wetlands  ‘were  formerly  of  considerable  significance’  in  lowlands  of  England  and  Wales  [Lewin,  p.  267].    From  Merri:s  et  al,  2011,  Anthropocene  streams  

Lewin,  J.  2010  Medieval  environmental  impacts  and  feedbacks:  The  lowland  floodplains  of  England  and  Wales.  Geoarchaeology  25,  267–311.    

A  remnant,  late  Pleistocene-­‐Holocene  tussock-­‐sedge  wet  meadow  

The  Great  Marsh  –  A  Rare  Ves&ge  of  a  Late  Pleistocene-­‐Holocene  Wetland    

Paleoecologist  C.  Grand  Pre  and  Palynologist  C.  Bernhardt  

The  Great  Marsh  –  A  Rare  Ves&ge  of  a  Late  Pleistocene-­‐Holocene  Wetland    

Top                                

Bo\om  

9580  +/-­‐  40  BP  Cal  BP  11130  to  10740  

Alaskan  Periglacial  Valley  and  Slopes    (analog  for  mid-­‐Atlan&c  Pleistocene  condi&ons)  

Photo  Courtesy  Ellen  Wohl    

Coarse  gelifluc&on  deposits  fill  small  valley  bo\om  

Holocene  Wetland  plants  and  organic  muck    accumulate  at  groundwater  seeps/springs.  

Small  channels.  

Alaskan  Periglacial  Valley  and  Slopes    (analog  for  mid-­‐Atlan&c  Pleistocene  condi&ons)  

Photo  Courtesy  Ellen  Wohl    

Millpond  sediments  bury  periglacial  toe  of  slope  and    

wetland  VB  deposits  

Incised  channel  post-­‐dam  breach.  

Coarse  gelifluc&on  deposits  fill  small  valley  bo\om  

Reconstruc&ng  Original  Holocene  Wetland  Condi&on  

1  mm  

160±  40  

140±  40  

90  ±  40  

270  ±  40  230  ±  40  

230  ±  40  850  ±  40  

1220  ±  40  

2860  ±  40  3000  ±  40  

All  but  one  date  on  single  nut.  

Big  Spring  Run,  PA,  Buried  Wetland  Soil    Radiocarbon  (AMS)  Dates  and  Paleo-­‐seed  Sampling    

European  se\lement  1709  

Paleo-­‐seed    sample  column  

0                  170  cm  

Paleo-­‐seed  Analysis:  Changes  in  Seeds  with  Depth  (Time)  

•  89  cm  of  sediment  sampled  at  2-­‐cm  intervals  

•  2,485  seeds  extracted    •  1,547  seeds  idenSfied  •  938  seeds  unidenSfied    •  38  plant  species  idenSfied    

A.   Neugebauer,  F&M  Honors  Thesis  2011;    M.  Voli,  F&M  Thesis,  2008;  W.  Hilgartner  (Johns  Hopkins)  and  J.  HartranS  (PA  DEP)  

Glyceria  striata  (Fowl  manna  grass)  

Eleocharis  obtusa  (blunt  spikerush)  

1  mm  

Carex  prasina  type  (n  =165)  -­‐drooping  sedge  Obligate  wetland  perennial  

0   2   4   6   8   10   12   14   16   18   20  72  76  80  84  88  92  96  

100  104  108  112  116  120  124  128  132  136  141  147  157  

Number  of  Seeds  

Depth  (cm)  

   250  BP*-­‐European  Contact  795  BP    1540  BP    3000  BP    

Wet  Meadow  

72  

80  

88  96  

104  

112  

120  

128  

136  

144  

152  

160  

Depth,  cm  

Eleocharis  obtusa  (n  =  125)-­‐  blunt  spikerush    Obligate  wetland  perennial    

0   10   20   30   40   50   60   70   80  72  76  80  84  88  92  96  

100  104  108  112  116  120  124  128  132  136  141  147  157  

Number  of  Seeds  

Depth  (cm)  

   250  BP*-­‐European  Contact  795  BP    1540  BP    3000  BP    

Mud    Flat  

72  

80  

88  96  

104  

112  

120  

128  

136  

144  

152  

160  

Depth,  cm  

Wet  Meadow  

Alisma  plantago  (n  =27)-­‐  water  plantain  Obligate  wetland,  aqua&c  (up  to  15-­‐cm  water  depth)    

0   1   2   3   4   5   6   7   8  72  76  80  84  88  92  96  

100  104  108  112  116  120  124  128  132  136  141  147  157  

Number  of  Seeds  

Depth  (cm)  

Transgression  (higher  water)  Not  just  increase    in  sed  supply  

   250  BP*-­‐European  Contact  795  BP    1540  BP    3000  BP    

Pond  

Mud    Flat  

72  

80  

88  96  

104  

112  

120  

128  

136  

144  

152  

160  

Depth,  cm  

Wet  Meadow  

How  to  Restore  to  “Target”  

04/2013  

Before:    04/2005  

Aeer:    04/2013  

0    0                            0.25                        0.5  km  

Big  Spring  Run  Floodplain/Wetland  Restora&on  Sta&s&cs  

NCALM  lidar  DEM  

•  Watershed area: 4.3 km2

•  Length Restored: 915 m

•  Mass Removed: ~20,000 tonnes

•  Area of Wetland Created: 1.6 ha N

Restora&on  Reach  

Map  Boundaries    and  Depth  of  Historic  Sediment  and  

Reconstruct  Extent  of  Original  Wetland  

 •  Trenching  •  Coring  •  Mapping  incised  

banks  

New  Channel(s)  and  Floodplain  

BSR  Stream  Bank  Excava&on  

Began  September  2011  

Big  Spring  Run  Floodplain    Wetland  Restora&on  WebCamera  

Completed November 2011- Designed and Engineered by LandStudies Inc.

Wetland-­‐Floodplain  Restora&on  Experiment,  Big  Spring  Run,  PA  

Restora&on  by  LandStudies,  Inc.,  Li&tz,  PA  

Pre-­‐restora&on  (March  2011)  

During  restora&on  (October  2011)  

Big  Spring  Run  View  West  

Before  Excava&on  9/13/11   Aeer  Excava&on  9/28/11  

Objec&ve:  Reconnect  the  groundwater  with  a  low,  hydric  floodplain.  Increase  hyporheic  exchange,  storage  of  OM,  and  interacSon  with  DOC.  

Big  Spring  Run  View  East  

Before  Excava&on  9/13/11   Aeer  Excava&on  9/28/11  

Objec&ve:  Remove  the  impairment…  the  eroding  stream  banks  that  contribute  to  high  suspended  sediment  and  nutrient  loads,  and  permit  frequent  OB  flow.  

Big  Spring  Run  Aeer  Restora&on  April  2013  

Before Restoration April 2005

Big  Spring  Run  Before  Restora&on  April  2005  

Big  Spring  Run  Aeer  Restora&on  November  2011  

Post-­‐Restora&on  August  2013  

Pre-­‐  and  Post-­‐Restora&on  Monitoring  

Big Spring Run Floodplain Wetland Restoration

See video of 18 September 2012 flood at http://www.youtube.com/channel/UCorgwKIsH03jLRuTSF3Wxzg

Aerial  views  Pre-­‐  and  Post  

04  14  2007   06  04  2013  

0    0                            0.25                        0.5  km  Hydrogeology:  18  piezometers,  32  shallow  wells  Q,  T,  flow,  pH,  DO,  DOC,  N,  P      3  USGS  Gage  Sta&ons  3  ISCO  samplers  3  Turbidity  sensors      

Monitoring  H2O,  Sed  &  Nutrients  In  and  Out:  Pre-­‐  and  Post-­‐Restora&on    

NCALM  lidar  DEM  

East Branch

West Branch

Main Stem

N

Restora&on  Reach  

Channel Cross Section Surveying  

Mapping  &  Surveying  Stream  Banks  

Pre-­‐se\lement  Wet  Meadow  and  Modern  Anthropocene  Stream  Measuring  Rates  of  Erosion  and  Deposi&on  2004  -­‐  present  

Repeat  high-­‐resolu&on  topographic  surveys,  Big  Spring  Run,  PA  Shilling,  2010,  and  Becker,  2011  (F&M);  Collabora&on  with  A.  Gellis,  USGS  

2004  

Cross  sec&on  

Cross  sec&on  

Measuring  Rates  of  Erosion  and  Deposi&on  2004  -­‐  present  

Repeat  high-­‐resolu&on  topographic  surveys,  Big  Spring  Run,  PA  Shilling,  2010,  and  Becker,  2011  (F&M);  Schulte,  Blair,  and  Lewis,  2013  (F&M);  Collabora&on  with  A.  Gellis,  USGS  

Grain  Size  Analysis  Stream  Banks:    ~100%  silt,  v.f.  sand,  and  clay  

Bars  along  incised  corridor:    ~10-­‐20%  sand  or  finer  

Bank

Point Bar

0    0                            0.25                        0.5  km  

%  Contribu&on  from  Stream  Banks  -­‐  Chemical  Fingerprin&ng  

NCALM  lidar  DEM  

Sweeney Gage

Fry Gage

Keener Gage

N Mean  =  63%  

Mean  =  54%  

Mean  =  33%  

0   100  %  

0   100  %  

0   100  %  

Inset  Point  Bars  

“Floodplain”  1.  80-­‐100%  of  deposiSon  on              “Sle  pads”  on  inset  point            bars  is  from  bank  erosion.  

%  Bank  Erosion  

2.  No  deposiSon  on  Sle    pads            on  “floodplain”  (i.e.,  on            legacy  sediment  terrace).  

Tile  Pad  Experiment  –  Where  Does  Deposi&on  Occur?    

 •  Discharge  •  Turbidity  •  Suspended  sediment  loads  •  Loud  out  –  Load  into  restora&on  reach  

USGS  Gage  Data  

Out  –  In  <    0    No  erosion,  Yes  deposi&on  

Out  –  In  <    0    No  erosion,  Yes  deposi&on  

Out  –  In  <    0    No  erosion,  Yes  deposi&on  

Pre-­‐  and  Post-­‐Restora&on  (Out  –  In)  

Legacy Sediment Removal/Riparian Wetland Restoration Best Management Practice

•  The BMP proposed by PADEP is an ecological restoration and management strategy. •  Restoration and management actions are proposed to re-establish

natural stream, wetland, floodplain and riparian conditions and functions. •  Monitoring at BSR and future implementation sites are necessary to fully quantify and document the BMP benefit (i.e., load reduction). •  Contact Jeff Hartranft, PADEP: [email protected]

Collaborators  include    •     37  researchers,    •     11  ins&tu&ons    •     3  agencies            PA  DEP,  EPA,  USGS  •         4  graduate    •         ~22  undergrad    •       Restora&on  by              LandStudies,  Inc.  

Ongoing  Research  at  BSR  


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