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Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection Agency Cincinnati, OH

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Page 1: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Treatment OptionsPart 1

Tom Sorg Darren Lytle

Water Supply and Water Resources DivisionOffice of Research and Development

U.S. Environmental Protection AgencyCincinnati, OH

Page 2: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Topics – Part 1

• Arsenic Chemistry

• BAT Technology

• Adsorptive Media

Page 3: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Arsenic Chemistry

Arsenic Species As (III) - H3AsO3

0 , H2AsO3-1 , HAsO3

-2

As (V) - H3AsO40 , HAsO4

-1 , AsO4-2

Page 4: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Arsenic Chemistry

What is the significance of arsenic speciation?

As V more effectively removed than As IIIby most treatment technologies

Page 5: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Arsenic Occurrence

Surface waters - predominantly As (V)

Ground waters – usually found as As (III), however, it can As (V) or a combination ofAs (III) and As (V).

Page 6: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

For maximum As removal

oxidize As (III) to As (V)

before applying treatment

Arsenic Chemistry

Page 7: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

As III Oxidation

Effective!

Free Chlorine

Potassium Permanganate

Ozone

Solid Oxidizing Media (MnO2 solids)

Ineffective

Chloramine

Chlorine Dioxide

UV Radiation

Page 8: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Oxidation of As III by aeration

not effective

Page 9: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Topics – Part 1

• Arsenic Chemistry

• BAT Technology

• Adsorptive Media

Page 10: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Arsenic Rule

Best Available Technology (BAT)Technology Maximum Percent

Removal (As V)Ion Exchange 95Activated Alumina 90Reverse Osmosis >95Modified Coag/Filtration 95Modified Lime Softening 80Electrodialysis Reversal 85Oxidation/Filtration (20:1 Fe/As) 80

Page 11: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Arsenic Rule Other Ground Water Processes

Technology Reason for not being listed as BAT

Coagulation Assisted No full scale historyMicrofiltration

Granular Ferric Lack of published dataHydroxide (GFH)

Page 12: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Small Systems Compliance Technologies Centralized Treatment – IE, AA, MC/F, MLS, Fe Removal

POU - RO, Activated Alumina

POE – Activated Alumina

Arsenic Rule

Page 13: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Arsenic Treatment - Process Selection Guide

Iron - mg/L

0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0

Ars

enic

- u

g/L

0

5

10

15

20

25

30

35

40

45

50

As MCL

Fe

- S

MC

L

A

Iron Removal Process(Optimized for Maximium As Removal)

BModified Iron Removal Process

C

Media AdsorptionIron Coag/FiltIon ExchangeIron Removal(M)RO / NF

20 - 1 Fe/As ra

tio

or above

Page 14: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Topics – Part 1

• Arsenic Chemistry

• BAT Technology

• Adsorptive Media

Page 15: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Arsenic Demonstration Program – Round 1

Technologies selected for demonstration (12 sites)

Adsorptive media – 9Iron media – 7 (E 33, Sorb 33, GFH)Iron based media – 1 (G2)Modified activated alumina –1 (AAFS 50)

Ion exchange – 1 (As & NO3)Iron removal – 1Treatment modification (iron removal process) - 1

Page 16: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Adsorptive Media Processes

Advantages• Simple process• High removal capacity• Non hazardous waste products• Low cost

Page 17: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Adsorptive Media Treatment

Disadvantages• Removal capacity impacted by water chemistry, such as pH• pH adjustment may be required• Media replacement

Page 18: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Adsorptive Media Treatment

Key design factors• Media• Bed configuration

Page 19: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Adsorptive Media Listed in NSF/ANSI STD 61

Company Base Material Name Material

Alcan (4) Aluminium AAFS - 50 Mod AA

Alcoa (2) Aluminium CPN AA

Apyron Aluminium Aqua-Bind Mod AA

Engelhard Aluminium ARM 100 AA

Engelhard

ADI Internat.

Iron

Iron

ARM 200

G2

Iron Oxide

Iron based

SMI Iron SMI III Iron/sulfur

US Filter Iron GFH Iron Hydroxide

Bayer AG Iron E 33 Iron Oxide

WRT Zeolite Z – 33 Mod Zeolite

Magnesium Elektron

Zirconium Isolux Zirconium Hydroxide

Page 20: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Figure 1. Results of Arsenic Removal by Adsorptive Media Pilot Plant Studies.

Bed Volumes X 1000

0 5 10 15 20 25 30 35 40 45 50 55 60 65

Ars

enic

Co

nce

ntr

atio

n -

ug

/L

0

5

10

15

20

25

30

35

40

45

50

55

60

MCL

C2 Alcan Modified AAC3 ADI G2

C1 Alcoa CPN AA

C4 E33 C5 Englehard Modified AAC6 GFH

Page 21: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection
Page 22: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Adsorptive Media System Designs

Simple 1, 2, or 3 beds in parallel

Page 23: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

A A

Adsorptive Media System Design

Roughing filter

Polishing filterBB

Series Design

Page 24: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Activated Alumina System - New Hampshire

Page 25: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Arsenic Removal, Activated Alumina System(CS), NH. 1998-99

Week

0 5 10 15 20 25 30 35 40 45 50

Ars

enic

con

cent

ratio

n -

ug/L

0

10

20

30

40

50

60

70

80

Influent water After 1st AA tank After 2nd AA tank System effluent

Influent water: pH 8.2, alk 58 mg/L (CaCO3), Fe <0.03 mg/L

Page 26: Treatment Options Part 1 Tom Sorg Darren Lytle Water Supply and Water Resources Division Office of Research and Development U.S. Environmental Protection

Adsorptive Media TreatmentFlow Media

gpm

Design Total Capital Investment (TCI)

Equipment Cost

Eq Cost

% of TCI

70 G2 Series $154,700 $102,600 66

37 AAFS50 Series $228,309 $122,646 54

45 E33 Series $90,757 $66,235 73

100 E33 Parallel $106,568 $82,081 77

145 E33 Parallel $139,251 $112,211 80

300 E33 Parallel $211,000 $129,500 62

320 E33 Parallel $153,000 $112,600 73

350 GFH Parallel $232,309 $157,646 68

640 E33 Parallel $305,000 $218,000 71