Arsenic: USEPA Demonstration Program
and Latest Research Results
Tom Sorg
USEPA
Cincinnati, OH
Workshop on Inorganic Contaminant Issues
August 21-23, 2007
Cincinnati, OH
Topics
•Short Summary of USEPA Arsenic Demonstration Program •Latest Research
USEPA Arsenic Demonstration Program
• $23 million will have been funded on the arsenic demonstration program. ($12M EPA; $11M Congress) • Three sets of projects (50 sites): Round 1 – 12 demonstration projects Round 2 – 28 demonstration projects Round 2a – 10 demonstration projects • Focused on commercially ready technologies or engineering approaches
Arsenic Demonstration Projects
50 projects – 26 States
States No. of Sites States No. of Sites
ME NH VT CT NY DE MD PA OH MI WI IL MN 3 3 1 2 1 1 1 1 2 3 2 2 4 ND SD LA TX NM AZ UT ID NV MT WA OR CA 1 1 1 3 3 3 1 2 1 1 1 2 3
Arsenic Demonstration Sites (50) 26 States
* VT
WA OR
ME
* *
NH MA
*
MT ND
***
*
*
NV
*
CA
* ID *
*
SD WY NE
* MN * ** *
IA
NY
*
WI
CT NJ
MD
*
UT CO KS MO AZ
**
* *MI * * * * * * OH IL * * IN * *
KY TN
PA
*
* * DE
MD
WV VA NC SC
**
*
NM
* * *
TX
OK
AR LA MS AL GA
*
*
*
*
FL
Arsenic Removal Technologies – 50 projects (Rd 1& 2)
Technologies Adsorption media Adsorptive media w/ Pretreatment (IR) Iron Removal Coagulation/Filtration Ion Exchange (NO3) POU - RO RO System Modification (Iron Removal) To be selected Total 26 2 12 3 2 1 1 1 2
Adsorptive Media
Adsorption Media Products (10) E33S & E33P GFH ATS Complex 2000 IsoluxTM ArseneXnp ARM 200 AAFS 50 G2 ADSORBSIA KemIron
Arsenic Demonstration Program – 50 Projects
Program Round 1 Round 2 Round 2a TOTALS Sites 12 28 10 50 Systems Installed 12 25 0 37 Studies Completed 7 14 0 21 Progress Reports 10 11 0 21 Final Reports 2 2 0 4
Reports provided on EPA web page at: http://www.epa.gov/ORD/NRMRL/wswrd/dw/arsenic/
Latest Research Results
•Questions/Responses •Future
Common Questions / Responses Question 1 What was basis for equipment selection?
Common Questions / Responses
Question 1 – Response
Major Considerations
Water Quality – Iron / Arsenic / Co-contaminants Residuals – Type/Quantity and Disposal Options Available System Operating Cost
Arsenic Removal Technologies
Major Player Iron “a very effective adsorber of arsenic”
Rule of Thumb Removal of 1 mg/L of iron achieves removal of 50 ug/L arsenic (Optimized condidtions)
Iron common to many ground waters! Removal of iron leads to removal of arsenic!
Arsenic Removal Technology Selection Guide Based Upon the Arsenic and Iron Concentration in the Source Water.
50
Fe SMCL
45
B
Modified Iron Removal Process
Arsenic Concentration -ug/L
40 35 30 25 20 15 10 5 0 0.0 0.1 0.2
C
Media Adsorption Ion Exchange Iron Coag/Filtration Iron Removal (M) Membrane Process
Fe tio Ra s /A of
/ 20
1
A
Iron Removal Process Optimized for As Removal
As MCL
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1.0
Iron Concentration - mg/L
Arsenic Removal Technology Selection Guide Based Upon the Arsenic and Iron Concentration in the Source Water.
50
Fe SMCL
45
B
Modified Iron Removal Process
Arsenic Concentration -ug/L
40 35 30 25 20 15 10 5 0 0.0 0.1 0.2
C Low Iron
Media Adsorption Ion Exchange Iron Coag/Filtration Iron Removal (M) Membrane Process
Fe
tio Ra s /A
of
/ 20
High Iron
A
Iron Removal Process Optimized for As Removal
1
As MCL
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1.0
Iron Concentration - mg/L
Technologies – Raw Water Arsenic/Iron Concentrations
Site 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 As ug/L 25 34 30 17 34 27 25 27 20 16 146 42 14 29 39 14 15 Fe mg/L 3.10 3.00 2.60 2.48 2.10 1.80 1.60 1.55 1.50 1.40 1.33 1.30 0.90 0.81 0.55 0.50 0.33 Tech. IR IR IR AM IR IR IR/AM IR IR IR IR IR/AM IR IR IR IR Site 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 As ug/L 19 25 50 28 52 14 37 19 18 14 30 36 26 56 30 33 33 Fe mg/L 0.27 0.25 0.17 0.16 0.13 0.13 0.13 0.10 0.07 0.06 0.05 0.05 0.40 0.03 0.02 0.02 0.02 POU AM AM AM CF AM CF AM AM AM AM AM AM Tech. AM AM AM Site 35 36 37 37 39 40 41 42 43 44 45 46 47 48 49 50 As ug/L 35 15 56 33 17 37 29 33 41 44 88 21 25 25 24 62 Fe mg/L 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 Tech. AM AM CF AM IE AM AM AM AM IE AM AM AM RO AM AM
Technology Selection Verses Raw Water As/Fe Concentrations
100 90 0.3 mg/L Fe SMCL Iron Removal Systems Adsorptive Media Coagulation/Filtration
Arsenic Concentration - ug/L
80 70 60 50 40 30 20 10 0 0.0 0.5 1.0 1.5 2.0
2.5
3.0
3.5
Iron Concentration - mg/L
Common Questions / Responses Question 1 – Response Major Considerations
Water Quality – Iron / Arsenic / Co-contaminants Residuals – Type/Quantity and Disposal Options Available System Operating Cost
Residuals
Technology Liquids Adsorptive Media Iron Removal Coagulation/Filtration Ion Exchange Reverse Osmosis Backwash Water w/ Solids (Possible) Backwash Water w/ Solids Backwash Water w/ Solids Regeneration Brine Reject Water Residuals Solids Exhausted Media
Residuals Disposal Options
Backwash Water Sewer Ground - Direct Septic System Recycle Evaporation/Holding Pond IE Brine/ RO Reject Water Sewer Septic System Evaporation/Holding Pond Adsorptive Media (Exhausted) Landfill Regeneration (on /off site)
Holding (?)Pond
Recycle Tank
Residual Disposal Methods Used
Residuals Disposal Method Sewer – 8 Ground – 1 Septic System – 1 Recycle / Sewer – 2 No BW – 6 Ground – 5 Sewer – 5 Recycle – 2 Septic System – 1 Sewer – 1 Holding Pond - 1
Iron Removal Backwash Water Coagulation/ Filtration Backwash Water
Adsorptive Media Backwash Water
Ion Exchange Brine
Common Questions / Responses
Question 1 – Response
Major Considerations
Water Quality – Iron / Arsenic / Co-contaminants Residuals – Type/Quantity and Disposal Options Available System Operating Cost
Operational Cost Major Factor in Selection of Coagulation/Filtration Systems!
Technology Selection Verses Raw Water As/Fe Concentrations
100 90 0.3 mg/L Fe SMCL Iron Removal Systems Adsorptive Media Coagulation/Filtration
Arsenic Concentration - ug/L
80 70 60 50 40 30 20 10 0 0.0 0.5 1.0 1.5 2.0
2.5
3.0
3.5
Iron Concentration - mg/L
Common Questions / Responses Question 2 Are adsorptive media arsenic removal capacities meeting manufacturers estimates?
Common Questions / Responses
Question 2 – Response
Base upon experience of the arsenic demo program
some are, but many are not!
Performance Adsorptive Media (As V)
Site A B C D E F G H I J K As ug/L pH Units SiO2 mg/L 39 45 31 88 33 33 41 64 23 19 14 8.3 7.8 8.4 7.4 7.9 6.9 7.7 6.9 7.1 7.7 7.3 7.3 11 13 14 69 30 26 19 25 35 14 8 PO4 mg/L <0. 05 <0.05 <0.03 <0.1 <0.03 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 BVs to 10 ug/L 5,500 5,400 6,000 7,500 12,000 20,000 7,000 25,000 40,000 40,000 (1ST) 41,000 (2nd) >62,000 >68,000
Common Questions / Responses Question 3 If adsorptive media process has been selected for the treatment system, how
does one select the adsorptive media?
Common Questions / Responses
Question 2 – Response
Major Considerations
Performance – BVs (removal capacity) - Time (replacement) Cost – Media & media replacement Residuals – Backwash water disposal options
Spring Brook MHP, Wales, ME (ATS Media)
SP Oxidation
Columns
SP
Tanks 1 1+2 1+2+3 BV Cu ft 1.5 3.0 4.5 EBCT min 2.2 4.4 6.6
1
1
SP
Design flow – 14 gpm Actual flow - 10.4 gpm Backwash water - none As – 38 ug/l (90% As III) pH – 8.5
2
2
SP
3
3
SP SP
Spring Brook MHP, Wales, ME
Arsenic III Removal by Adsorptive Media (ATS) at Spring Brook MHP, Wales, ME
70
60
Arsenic Concentration - ug/L
50
40
30
5000 BVs
20
10
MCL
0 0 2 4 6 8 10 12 14 16 18 20 22 24 26
Time - Weeks
Raw Well Water After Oxidation Tank After AM Tank 1 After AM Tank 2 After System - Tank 3
Replacement Cost $755/Column $915 Labor/travel $2,465 Total
Media Cost
$5.00 $4.50
$500/cf $400/cf
$4.00
$300/cf $200/cf
$3.50
$100/cf
Cost ($/1,000 gal)
$3.00
$2.50
$2.00
$1.50
$1.00
$0.50
$0.00 10 20 30 40 50 60 70 80 90 100
M edia Life (x1,000 Bed Volumes)
Arsenic III Removal by Adsorptive Media (E33) at Brown City, MI (May, 2004 to May, 2007)
30
Arsenic concentration - ug/L
25
20
Raw Water
15
10
Cl2 moved to before
MCL
5
treatment system
Treated Water
0 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75
Bed Volumes X 1000
Common Questions / Responses
Question 2 – Response
Major Considerations
Performance – BVs/Time Cost – Media & media replacement Residuals – Disposal of backwash water
No disposal option – Consider media/system that does require backwashing or 100% recycle
Latest Research Results
•Questions/Responses •Future
Adsorptive Media Systems
Future
System designs/equipment (most) allows for the use of a variety of media products. (EBCT major factor) Utilities will be switching to lower cost media products or to lower cost process (Coagulation/Filtration).
Adsorptive Media Pressure Tank
Freeboard Surface loading rate 5-9 gpm/sq ft Bed expansion 15 -50 %
Media EBCT 3 – 10 min
Bed depth 3-6 ft
Adsorptive Media System
Fiberglass Tanks
Results
AM System Operational Cost - $/1000 gal
Category Flow - gpm Media - cf Media Replacement Media Disposal Labor Total Cost Electricity $/1000 gal Labor $/1000 gal Media $1000 gal (est) Total $1000 gal NH 10 5 Lead TK $1,500 $200 $2,345 $4,045 0.001 0.33 6.00 6.33 $1,235 $2,785 0.001 1.80 15.00 16.80 VT 22 3 2 tanks $1,550 NM 320 160 (40K BVs) $24,000 $680 $2,120 $26,800 0.001 0.05 0.60 0.65 MD 320 160 (80K BVs) $24,000 680 $2,120 $26,800 0.05 0.07 0.30 0.43 $12,950 $70,550 0.001 0.18 5.00 5.18 NV 350 240 (7.5K BVs) $57,000
Adsorptive Media
(Cost Range - $70 to $500 cf)
Adsorption Media Products (10) E33S & E33P GFH ATS Complex 2000 IsoluxTM ArseneXnp ARM 200 AAFS 50 G2 ADSORBSIA KemIron
Arsenic III Removal by Adsorptive Media (ATS) at Spring Brook MHP, Wales, ME
70
60
Arsenic Concentration - ug/L
50
40
30
5000 BVs
20
10
MCL
0 0 2 4 6 8 10 12 14 16 18 20 22 24 26
Time - Weeks
Raw Well Water After Oxidation Tank After AM Tank 1 After AM Tank 2 After System - Tank 3
Replacement Cost $755/Column $915 Labor/travel $2,465 Total
RSSCT Study – Spring Brook NHP Site
(As 38 ug/L – pH 8.5)
Media KemIron GFH Adsorbia GTO ARM 200 (Old) ARM 200 (New) E33 ArsenXnp AAFS50 A/Complex 2000 RSSCT BVs to 10 ug/L 25,000 23,000 12,500 17,500 13,000 20,000 18,000 6,700 5,000-6,500 Full Scale System BVs to10 ug/L 11,500 8,500
Adsorptive Media System Changes
Site Spring Brook MHP Bow, NH STMIGID Original Media ATS G2 GFH ( 3 Tanks) New Media/Process KemIron & GFH AAFS50 GFH (1) KemIron (2) May convert to Coagulation/Filtration ARM 200 (Trial Run) Coagulation/Filtration Shut down because of high cost Shut down because of uranium (disposal)
Valley Vista Rollinsford, NH Desert Sands, NM Lake Isabella, CA
AAFS50 E33 E33 ArsenXnp
Results
IR System Operational Cost - $/1000 gal
Site MN WI MN MI System IR IR IRw/Fe add IRw/Fe add Flow gpm 20 45 140 150 Chemicals 0.12 (KMnO4) 0.16 (Cl2) 0.03 (FeCl3) ? Electricity 0.04 0.07 0.04 0.07 Labor 0.27 0.11 0.22 0.15 Total 0.43 0.33 0.29 0.22
Note - Disposal of residuals not included
Adsorptive Media Systems
Future
Some adsorptive media products can be regenerated
There are other products, particularly the iron based products, that are not currently being regenerated. Research starting on the regeneration of these products. Preliminary tests indicating that up to 85% of arsenic can be stripped off with caustic solution. Regeneration could lead to lower operating cost.
Media Regeneration
• Spent Media
including:
• GFH (2) • KemIron (1) • E33 (2) • ARM 200 (1) • Use 4% caustic solution
Results – Arsenic Demonstration Program
Performance Systems shown ability to reduced arsenic to below MCL Utilities have found most systems easy to operate Many systems have improved the general distribution water quality Change in water quality has not resulted in any Pb/Cu issues
Results – Arsenic Demonstration Program
Performance All spent throw-away media has passed TCLP tests Utility can switch adsorptive media products with out having to change adsorptive media equipment. Utility can switch adsorptive media system over to coagulation/ filtration system.
Acknowledgements
• Battelle Memorial Institute – Columbus OH • Water utilities participating in the arsenic demonstration program
Tom Sorg 513/ 569-7370 sorg.thomas@epa.gov
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