Permeable(Reac+ve(Barriers(for( Reduc+on(of(Nitrate(Discharge( … · PilotProjectTasks" •...

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` Permeable Reac+ve Barriers for Reduc+on of Nitrate Discharge from Sep+c Systems Preliminary Results from a Great Bay Pilot Study Danna Truslow, PG; Truslow Resource Consul;ng, LLC, RCCD Mark Kelley, PE; Haley & Aldrich, Inc.

Transcript of Permeable(Reac+ve(Barriers(for( Reduc+on(of(Nitrate(Discharge( … · PilotProjectTasks" •...

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Great  Bay  PRB  Pilot  Study  1  

Permeable  Reac+ve  Barriers  for  Reduc+on  of  Nitrate  Discharge  from  Sep+c  Systems  –    Preliminary  Results  from  a    Great  Bay  Pilot  Study    

Danna  Truslow,  PG;      Truslow  Resource  Consul;ng,  LLC,  RCCD  

Mark  Kelley,  PE;      Haley  &  Aldrich,  Inc.  

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Project  Purpose  

•  To  install  pilot  systems  and  test  effec;veness  of  Permeable  Reac;ve  Barriers  (PRBs)  in  the  Great  Bay  Watershed  for  nitrogen  removal  

•  To  gather  shallow  groundwater  quality  data  adjacent  to  exis;ng  sep;c  systems  to  determine  sep;c  system  nitrogen  contribu;on  

•  To  implement  effec+ve  nitrogen  removal  solu+ons  in  the  Great  Bay  Watershed  as  part  of  the  watershed  management  plan.  

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Project  Partners  

 Lead  Agencies  –  Rockingham  County  Conserva;on  District  and  Strafford  County  Conserva;on  District  

 Truslow  Resource  Consul+ng  LLC  –    Project  Management,  Hydrogeology  

 Haley  &  Aldrich  Inc.  and  Lombardo  Associates  –  Permeable  Reac;ve  Barrier  Design  and  Installa;on  

 Site  Owners  –  Durham  and  Brentwood  

 Towns  of  Brentwood  and  Durham  –    PRB  Construc;on  Manpower,  Equipment,  and  Materials  

     Absolute  Resource  Associates  -­‐  Laboratory  3   Great  Bay  PRB  Pilot  Study  

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Sep;c  Load  to  Great  Bay  Watershed  –    29%  of  Es;mated  Non  Point  Source  Load  

Source  :  Trowbridge,  et.  al.,  2014.    Great  Bay  Nitrogen  Nonpoint  Source  Study  4   Great  Bay  PRB  Pilot  Study  

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What  are  some  measures    that  can  be  taken  to  reduce    

nitrogen  loading  from  sep;c  systems?  

• Regularly  maintain  systems  and  pump  sep;c  tanks  

•  For  new  systems  site  properly  and  use  nitrate-­‐removing  systems  

• Control  inorganic  nitrogen  migra;on  from  sources  through  PRBs  and  other  passive  treatment  technologies.  

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Pilot  Project  Tasks  

• Well  installa;on  and  tes;ng  to  determine  site    hydrogeology  –  2014  

•  Pre-­‐  installa;on  GW  and  SW  design  sampling  and  baseline  monitoring  –  Year  2014,  2015  –  Nitrogen  species,  BOD,  dissolved  metals,  alkalinity,  field  measured  pH,  DO,  SC  

•  Brentwood  PRB  design  and  installa;on  –October  2015  

•  Durham  PRB  design  and  permidng  -­‐  2015,  Installa;on  2016  

•  Post  installa;on  monitoring  –  2015  and  2016  

•  Evalua;on  and  Outreach  –  2015  and  2016  

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Criteria  for  Project  Sites  

• Ac;ve  sep;c  system  

•  Shallow  groundwater  with  predictable  flow  path  •  Sandy  overburden  underlain  by  restric;ve  silt/clay  • Nearby  surface  water  • Willing  landowner  

• Accessible  site  for  PRB  installa;on  

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Site Locations

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Permeable  Reac;ve  Barrier  (PRB)  Demonstra;on:  Showing  Nitrate  Removal  Using  PRB  

50  FT  

110  FT  

5  FT  

8  FT  

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Wood Chip Bioreactors

•  Low-cost carbon source for denitrification

•  In-stream reactors and shallow subsurface reactive barriers are simple to install and maintain

Bacteria +C + N03 N2

(Carbon + nitrate) (nitrogen gas)

(Dr. Will Robertson, U. Waterloo, Canada) [email protected] 10   Great  Bay  PRB  Pilot  Study  

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Bioreactor for Treating Nitrate in Shallow Groundwater

http://www.lombardoassociates.com/ 11   Great  Bay  PRB  Pilot  Study  

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1, 2 and 8-yr-old woodchips

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Nitrate PRB Demonstrations Projects •  2  PRBs  installed  in  Waquoit  Bay,  

Massachuseks  in  July  2005  –  Reduc;ons  of  NO3  from  10  to  <0.1  mg/L  

•  2  PRBs  proposed  in  Durham  and  Brentwood,  New  Hampshire  

•  Many  addi;onal  site  at  University  of  Waterloo,  Canada  

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Groundwater Quality at Waquoit Bay Data Collected by Woods Hole MBL

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Design  Challenges  

Durham:    

Low  transmissivity  (shallow  groundwater  with  small  saturated  thickness)  and  fluctua;ng  groundwater  table  

Brentwood:  

Radial  flow  away  from  raised  leaching  fields  –  for  demonstra;on  of  PRB  a  finite  trench  will  be  designed  

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PRB Design Parameters

•  Understanding  of  Site  Hydrogeology:  Groundwater  velocity  about  0.1  n/day  at  both  sites  (Hydraulic  conduc;vity  is  about  4  x  10-­‐4  cm/sec)  

•  PRB  Residence  +me:    Func;on  of  removal  goal:  Published  Values  range  from  0.7  to  32  mg/L  N/day  

• Width  and  Depth  of  PRB:    Width  is  determined  by  specified  PRB  residence  ;me,  and  depth  by  site  specific  geology  

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Conceptual PRB Designs

•  Design  Parameter:  2  mg/L  N/day  Removal  

•  Residence  +me  of  10  to  20  days:    Groundwater  Travel  ;me  or  Groundwater  Velocity  is  about  0.1  n/day  at  Durham  and  Brentwood  Sites  

•  Design  Width  of  PRB  =  1.5  to  2.0  n  wide  for  a    10  to  20  days  Res.  Time    

•  Depth:    Durham  =  5  n.      Brentwood  =  8  n.  

•  Length:    Durham  =  50  n.      Brentwood  =  110  n.  

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Durham  Site  •  Near  Chesley  Brook  tributary    of  Oyster  River  

•  Failed  sep;c  close  to  house,    new  sep;c  2008  

•  Glaciomarine  sand  underlain  by  silt  

•  K  =  2x10-­‐4  to  9  x  10-­‐3  cm/s    

•  Nitrate  6.2  mg/L  at  one  field-­‐side  monitoring  well,  

•  Installa;on  Summer  2016?  

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Durham  PRB  Design:    50  n.  x  1.5  n.  x  5  n.  (deep)  

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Brentwood  Site  •  Near  Dudley  Brook,  tributary  of  Exeter  River  

•  Failed  sep;c  area  in  community  sep;c  field  

•  New  area  installed  in  2012  – Glaciomarine  sand  with  underlying  silt  

•  K  =  1.5x10-­‐4  to  3.6  x  10-­‐4  cm/s    

•  Nitrate  12  to  42  mg/L  at  wells  

•  1.9  mg/L  in  nearby  SW  

•  Installed  October  2015  

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Pond  flows  to  Dudley  Brook  

Community  Leachfield  

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Es;mated  Nitrate-­‐N  December  2014  

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Brentwood  PRB  Design:    110  n.  x  1.5  n.  x  8  n.(deep)  

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Construc;on  of  Brentwood,  NH    PRB  –  13  October  2015  

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PRB  Placement  and  Site  Restora;on  

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Monitoring  Results  

•  New  monitoring  wells  installed  in  and  just    downgradient  of  trench  

•  Nitrate-­‐Nitrogen  decline  in  and  near  trench  –  20  to  30  mg/L  pre  installa;on  –  Less  than  2  to  12  mg/l  in  and  adjacent  to  trench  –    four  months  post  installa;on  

•  Biological  Oxygen  Demand    –  Pre-­‐installa;on  concentra;ons  -­‐  <  0.5  to  15  mg/L  –  One  month  aner  installa;on  –  320  to  408  mg/L  in  or  near  trench  –  Four  months  aner  installa;on  –  32  to  85  mg/L  

•  Dissolved  Oxygen  –  4  mg/L  pre-­‐installa;on  to  <  1.0  mg/L  post  installa;on  at  near  trench  

•  Dissolved  metals  to  be  monitored  in  Fall  2016  

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Apparent  Extent  of  Nitrate  Treatment  

February  2016  

Nitrate  Concentra;ons  in  Wells  February  2016  

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Funding  for  this  project  was  provided  in  part  by  a  Watershed  Assistance  Grant  from  the  NH  Department  of  Environmental  Services  with  Clean  Water  Act  SecEon  319  funds  from  the  US  Environmental  ProtecEon  Agency  

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