Real-time Performance Monitoring of Chemical Fixation Treatment - - PowerPoint PPT Presentation
Real-time Performance Monitoring of Chemical Fixation Treatment - - PowerPoint PPT Presentation
Real-time Performance Monitoring of Chemical Fixation Treatment Paul R. Lear, Ph.D. Presentation Outline Real-Time Performance Monitoring for Chemical Fixation Why is it necessary? How is it done? Example of its applicability
October 23, 2012 2
Presentation Outline
- Real-Time Performance Monitoring for
Chemical Fixation
– Why is it necessary? – How is it done?
- Example of it’s applicability
– Glass Landfill Site in Monaca, PA
October 23, 2012 3
Chemical Fixation (or Stabilization)
- Converts contaminants in their least mobile,
soluble or toxic form
- Mix design is often based on laboratory
treatability testing
– One or two samples collected from a site – Assumed to be representative
- Contractor bases treatment on the results of
laboratory testing
October 23, 2012 4
The Real World
- Sites are not homogeneous
– Waste materials vary in terms of composition, contaminant levels
- Implementation of the mix design can be less
than successful due to this variability
– Performance monitoring is typically based on TCLP or SPLP leachability testing (minimum 2 days TAT) – Receive failing results and then have to determine why – Meanwhile processing needs to continue
October 23, 2012 5
Real-Time Performance Monitoring
- Many chemical fixation reagents rely on pH
control to some extent
– Determination of pH can be helpful in performance monitoring
- Mimicking TCLP or SPLP extraction and
determining equilibrium pH can provide real- time performance monitoring
October 23, 2012 6
“Mini”-TCLP or SPLP
- Start with 5 to 10 g of treated waste instead of
100 g.
- Utilize the same leaching solution
– TCLP Extraction Fluid Type 1 or 2 – SPLP East or West of Mississippi extraction fluid
- Utilize the same liquids:solids ratio
– 20 mL extraction fluid per g of treated waste
October 23, 2012 7
“Mini”-TCLP or SPLP (cont.)
- Extraction
time needs to be long enough so that near equilibrium conditions have been reached
4 5 6 7 8 9 10 11 12 200 400 600 800 1000 1200 1400 1600 Time (min) pH
Minimum Extraction Time
October 23, 2012 8
Real-Time Performance Monitoring
- Correlate
equilibrium pH to results from full and complete test to determine minimum pH to indicate passing result
4 5 6 7 8 9 10 11 20 40 60 80 100 120 140
Time (min) pH Treated with 3% EnviroBlend Retreated with an additional 0.5% Enviroblend Treated with 3% EnviroBlend Retreated with an additional 0.5% Enviroblend Treated with 3.5% EnviroBlend Retreated with an additional 0.25% Enviroblend
October 23, 2012 9
Real-Time Performance Monitoring
- Obtain
frequent samples during
- perations
to monitor performance and tweak mix design
4 5 6 7 8 9 10 11 20 40 60 80 100 120 140
Time (min) pH AM Sample Midmorning Sample Noon Sample (increased Enviroblend %) Not Likely to Pass Likely to Pass
October 23, 2012 10
Real-Time Performance Monitoring
- Treated
material with low pH needs to be retreated
4 5 6 7 8 9 10 11 20 40 60 80 100 120 140
Time (min) pH
Treated with 3% EnviroBlend Retreated with an additional 0.5% Enviroblend Treated with 3% EnviroBlend Retreated with an additional 0.5% Enviroblend Treated with 3.5% EnviroBlend Retreated with an additional 0.25% Enviroblend
October 23, 2012 11
Monaca Glass Project
- Waste glass, debris, and soils
disposed of in a ravine near Monaca, PA over a 50 year timeframe
- Surface water in the ravine
impacted by lead, primarily from the waste glass which failed TCLP for lead
- Responsible party agreed to treat
the 25,000 cy of glass and soils to make it RCRA non-hazardous, place it on-site, and cap
October 23, 2012 12
Monaca Glass Project (cont.)
- Treatability testing on several samples of the
site material suggested that it may be made RCRA non-hazardous if treated by 3% EnviroMag
– Not all samples were successfully treated with this mix design
October 23, 2012 13
Monaca Glass Project (cont.)
- Design involved
– Excavation, – Debris removal, – Size reduction to -1/2 inch, – Pugmill mixing with 3% EnviroMag – Compaction in 8 inch lifts to 95% maximum modified Proctor density
- Placed and compacted material
was to be capped with low permeability clay
October 23, 2012 14
Monaca Glass Project (cont.)
- Pilot testing consisted of ten 100 cy stockpiles of
excavated material, all treated with 3% EnviroMag
- Only 30% of the pilot- test stockpiles passed
(TCLP < 5 mg/L)
– Passing stockpiles contained only glass and little to no soil or debris – The more soil, the higher the TCLP-leachable lead and the lower the pH after the 18 hour TCLP extraction
- Retreatment with an additional 3% EnviroMag (6%
total) allowed failing stockpiles to pass
October 23, 2012 15
Monaca Glass Project (cont.)
- Client was not willing to proceed if 6% EnviroMag
required for the treatment
- WRScompass suggested that we could utilize real-
time monitoring to evaluate the treatment and minimize the EnviroMag usage
– Evaluate soil content of feed material to select a starting EnviroMag addition rate – Real-time monitoring on every 200 tons treated – Adjust EnviroMag usage based on real-time monitoring
- Oversight Engineer was skeptical, but agreed to let
us try
October 23, 2012 16
Monaca Glass Project (cont.)
- Real-time monitoring on every 200 tons
treated
– Determined near-equilibrium pH in TCLP Extraction Fluid #1 – Near-equilibrium pH above 9 was correlated to passing TCLP results – Stockpiles with near-equilibrium pH below 9 were set aside for re-treatment – Adjust EnviroMag usage up or down as necessary
October 23, 2012 17
Monaca Glass Project (cont.)
- Overall results of real-time monitoring
– 65% of the 200 tons stockpiles were cleared by real-time monitoring (35% required re-treatment) – More than 95% of the stockpile cleared by the monitoring had TCLP lead concentrations less than 5 mg/L – Over 95% of retreated stockpiles passed – EnviroMag usage ranged from 1.5% to 4.5% with an overall usage of 3.4%
October 23, 2012 18
CSX Benton Harbor Project
- Former scrap yard and
battery recycling
- peration adjacent to rail
line
- Disposal of battery
casings and lead plates
- n-site results in lead
contamination in soil and groundwater
October 23, 2012 19
CSX Benton Harbor Project (cont.)
- Approved Remedial Action
included:
– Excavation of all lead- impacted soil/debris – On-site stabilization to render the material non-hazardous – Transportation off-site for disposal as a non-hazardous waste – Backfill with clean fill and site restoration
October 23, 2012 20
CSX Benton Harbor Project (cont.)
- Contractor
chose to stabilize the excavated soil and battery casings using 5% Portland cement
October 23, 2012 21
CSX Benton Harbor Project (cont.)
- Early failure rate of 25%
- Contractor keep on treating piles
– Near 50% project completion, site was spoil- bound with piles of failed material
October 23, 2012 22
CSX Benton Harbor Project (cont.)
- CSX and EPA Region V
became concerned
- Review of operations
indicated that
– Variable soil:debris ratio likely cause of high failure rate – Real-time feedback to
- perations was required
October 23, 2012 23
CSX Benton Harbor Project (cont.)
- Real-time monitoring on
every pile during treatment
– Determined near- equilibrium pH in TCLP Extraction Fluid #1 – Near-equilibrium pH above 8 and below 11was correlated to passing TCLP results
October 23, 2012 24
CSX Benton Harbor Project (cont.)
- Stockpiles with near-
equilibrium pH below 8 or above 11 were set aside for re-treatment
– Piles below 8 had additional Portland cement added – Piles above 11 had additional waste added
- Remixed and resampled
retreated piles
October 23, 2012 25
CSX Benton Harbor Project (cont.)
- Overall results of real-
time monitoring
– All failed piles successfully treated (90% passed on 1st retreat) – Less than 5% of the pile cleared by the monitoring had TCLP lead concentrations greater than 5 mg/L (fail) – CSX, EPA Region 5, and contractor happy
October 23, 2012 26
Questions or Comments?
plear@wrscompass.com 865-919-5205
October 23, 2012 27 27