increased use of uv disinfection at potws and related ... increased use of uv... · landfill...

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1 Increased use of UV disinfection at POTWs and related issues with leachate pretreatment Michael Keen, E.I. Civil & Environmental Consultants, Inc. SC SWANA – 2014 Spring Conference May 7, 2014 POTW and the UV disinfection process Chlorination is still the most common form of disinfection ~75% of all major POTWs (1->100 MGD) UV usage rapidly growing among major POTWs 21% of all major POTWs currently use UV disinfection Between 2001-2005 about 40% of all UV systems in use as of 2009 were installed UV trend continuing due to safer work environment and the elimination of chlorine gas and/or chlorination/dechlorination

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Page 1: Increased use of UV disinfection at POTWs and related ... Increased Use of UV... · Landfill Pre-treatment Leachate traditionally high in organics, metals and nitrogen Typical treatment:

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Increased use of UV disinfection at

POTWs and related issues with

leachate pretreatment

Michael Keen, E.I.

Civil & Environmental Consultants, Inc.

SC SWANA – 2014 Spring Conference

May 7, 2014

POTW and the UV disinfection process

� Chlorination is still the most common form of disinfection� ~75% of all major POTWs (1->100 MGD)

� UV usage rapidly growing among major POTWs� 21% of all major POTWs currently use UV disinfection

� Between 2001-2005 about 40% of all UV systems in use as of 2009 were installed

� UV trend continuing due to safer work environment and the elimination of chlorine gas and/or chlorination/dechlorination

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UV Absorption

Organic matter

UV disinfection process

� Energy gets absorbed by the microorganisms and damages DNA

� Energy can get absorbed by background and not reach the organism� UV transmittance (UVT) and UV absorbance (UVA)� Transmittance of at least 65% is required

Pure water Leachate, wastewater or natural water

Organic content, Iron, UV absorbance

UV transmittance

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Typical Wastewater UV Transmittance

� Suspended growth processes – Activate Sludge� 60-65% UVT

� Fixed film processes- Trickling Filter� 50-55% UVT

� Sequencing batch reactor� 45-60% UVT

� Enhanced Primary � Alum – 40-50% UVT� Ferric- 25-45% UVT

� Tertiary filtration� 50-85% UVT

UNTREATED SOLID WASTE LEACHATE - HIGHLY VARIABLE

POTW and the UV disinfection process

Transmittance:

T = I / I0% Transmittance, %T = 100 T

Absorbance:A = log10 I0 / IA = log10 1 / T

T=10-A

I0 I

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Landfill Pre-treatment

� Leachate traditionally high in organics, metals and nitrogen

� Typical treatment:� pre-treatment includes precipitation and

biological treatment� Co-treatment with wastewater at POTW

� After Biological treatment� Most organic carbon in leachate is not

biodegradable further� Residual organic content may still be relatively

high� POTWs typically accept pre-treated leachate

with residual organics

UV disinfection is changing the STATUS QUO!

Solid Waste Leachate – Natural Organic Matter

� Humic Substances (HS)� Fulvic Substances (FS)� Hydrophilic Organic Matter (Hpi)

HS>FS>Hpi

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Solid Waste Leachate – Humic Substances

� Humic Substances = paper, wood, yard waste

� Humic Substances – not directly assessable by common analytical methods due to heterogeneous molecular structure

Solid Waste Leachate – Humic Substances

� Humic Substances have chromophores which absorb UV light� Not removed during landfill pre-treatment� The low UV Transmittance and non-biodegradable

component of leachate

� Fulvic Substances – are organic matter with lower molecular weight and higher oxygen content� Usually associated with the remnants of dead cells

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Solid Waste Leachate - Age

� Early Age Leachate� High COD, TOC and BOD

� Higher BOD/COD ratios

� Older Leachate� Lower BOD/COD ratios

� Increased concentration of higher molecular weight humic and fulvic-like constituents

Color and UV Absorbance

� You can’t estimate UV Transmittance levels simply by the color of the leachate

� Color can indicate the presence of organics such as tannins and humic material

� Some organics and other matter that cause low UV Transmittance do not add any visible color to the leachate

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Color and UV Absorbance

0.00.10.20.30.40.50.60.70.80.91.0

200 300 400

Ab

sorb

ance

Wavelength, nm

cardboard leachate

cellulose-based dietary fiber

UV disinfection relevant wavelengths

Color producing wavelengths

(yellow)

(clear)

Color and UV Absorbance

200 250 300

Wavelength, nm

� Most common lamp type � Low pressure mercury vapor� Emission at 254 nm

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Dilution as Solution

� High strength leachate can have zero transmittance even after MBR treatment� Can constitute 1/200th of the wastewater flow or less to

comply with UVT requirements of POTW� Absorbance changes linearly with dilution (Beer-Lambert Law)

� Sample with A=1.0 will have A=0.1 at 1:10 dilution� A=1 � 90% of UV is absorbed in 1 cm of depth� A=2 � 99%; A=3 � 99.9%, etc.� Transmittance does not change linearly

0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

200 300 400 500 600 700 800

UV

abs

orba

nce,

cm

-1

Wavelength, nm

No dilution

1:10

1:50

0

20

40

60

80

100

120

200 300 400 500 600 700 800

UV

tra

nsm

itta

nce,

%

Wavelength, nm

No dilution

1:10

1:50

Dilution as Solution

� Leachate shown has absorbance of 40� 99.999999……….999% of light absorbed

� Spectrophotometers have a measuring limit of 3-4� Only reliably report 99.9% or 99.99% absorbance� Sample with 99.99999999999999% absorbance will

read as 99.99% because this is the instrument max� Samples need to be diluted until absorbance is

<99% and undiluted absorbance is back calculated

0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

200 300 400 500 600 700 800

UV

abs

orba

nce,

cm

-1

Wavelength, nm

No dilution

1:10

1:50

Instrument cutoff

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Treatment options

� Oxidation� Fenton’s� Ozone� Ozone + hydrogen peroxide

� Adsorption� Zeolite

� Membrane filtration� Nanofiltration� Reverse osmosis

Treatment options

� Fenton’s� Limited effectiveness� Sludge generation� Addition of high amounts of iron and H2O2� Potential COD removal (was not measured)

0

20

40

60

80

100

120

200 300 400

Tran

smit

tan

ce, %

Wavelength, nm

No treatment30 min120 min

254 nm

Minimum transmittance

Biologically treated leachate before Fenton’s

After 120 min of Fenton’s and 30 min of settling

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Treatment options

� Ozone and Ozone/H2O2� Limited effectiveness� Improvement with H2O2 addition� Bonus COD removal� Still not enough improvement in

high volume, high strength leachate

0%5%

10%15%20%25%30%35%

0 100 200 300Imp

rove

men

t in

UV

-T

Time, minOzone onlyOzone and hydrogen peroxide

0%20%40%60%80%

100%120%140%

0 100 200 300C

OD

, mg

/L

Time, minOzone onlyOzone and hydrogen peroxide

Before O3 O3/H2O2

Treatment options

� Zeolite (Ahlstrom Disruptor)� Limited effectiveness

0%

10%

20%

30%

40%

50%

60%

70%

0 100 200 300 400

UV

-T

Leachate dilution ratio in effluent with 65% UV-T

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Treatment options

� Membrane filtration� Nanofiltration � Reverse osmosis

� RO is highly effective� Energy expenditures� Membrane fouling� Concentrate management

0%

10%

20%

30%

40%

50%

60%

70%

0 50 100

UV

-T

Leachate dilution ratio in effluent with 65% UV-T

Hydronautics

Trisep

RO membrane

Nanofiltration membrane 1

Nanofiltration membrane 2

Raw leachate

After nanofiltration

Conclusions

� Leachate reduces the POTW UV Transmittance even after pre-treatment

� Most current pre-treatment are not effective in removing or reducing humic acids

� Pre-treatment of landfill leachate may be required for POTW to meet NPDES permit requirements or for their UV disinfection process to work effectively

� No one-size-fits-all solution currently available

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References

1. Leong, Lawrence Y.C., Kuo, Jeff, Tang, Chi-Chung 2009. Disinfection of Wastewater Effluent: Comparison of Alternative Technologies, Executive Summary: Water Environment Research Foundation.

2. Renou, S.; Givaudan, J. G.; Poulain, S.; Dirassouyan, F.; Moulin, P., Landfill leachate treatment: Review and opportunity. Journal of Hazardous Materials 2008, 150 (3), 468-493.

3. Zhao, R.; Gupta, A.; Novak, J. T.; Goldsmith, C. D.; Driskill, N., Characterization and treatment of organic constituents in landfill leachates that influence the UV disinfection in the publicly owned treatment works (POTWs). Journal of Hazardous Materials 2013, 258–259(0), 1-9.

4. Campagna, M.; Çakmakcı, M.; Büşra Yaman, F.; Özkaya, B., Molecular weight distribution of a full-scale landfill leachate treatment by membrane bioreactor and nanofiltration membrane. Waste Management 2013, 33 (4), 866-870.

5. US Environmental Protection Agency, Municipal solid waste in the United States: 2011 facts and figures. 2013.

6. UV photo online source: http://www.wedeco.com/us/expertise/uv-technology/uv-disinfection.html

7. Humic Substance photo online source: http://www.xsyagri.com/portfolio/potassium-humate/8. Bacteria photo online source:9. Credit: Daniel Nelson, UMD: http://www.cos.gatech.edu/news/Study-Quantifies-the-Size-of-

Holes-Antibacterials-Create-in-Cell-Walls-to-Kill-Bacteria10. Landfill Leachate photo online source:

http://www.reading.ac.uk/geographyandenvironmentalscience/Postgraduatetaught/ges-pgt-msc-soils-environmental-pollution.aspx

Questions?

Michael Keen, E.I.Civil and Environmental ConsultantsVoice: (980) [email protected]