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May 21-23, 2015 Athens TREATING MICROPOLLUTANTS OF EMERGING CONCERN: A CASE OF TRICLOSAN Filiz B. Dilek Middle East Technical University Dept. of Environmental Engineering Ankara, Turkey Industrial Waste & Wastewater Treatment & Valorization

TREATING MICROPOLLUTANTS OF EMERGING CONCERNuest.ntua.gr/iwwatv/proceedings/presentations/22... · Applied ozone (mg) TCS removal (%) Ozone dose (mg/L) 10 mn 5 min 1 min 10 mn 5 min

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May 21-23, 2015 Athens

TREATING MICROPOLLUTANTS OF EMERGING CONCERN:

A CASE OF TRICLOSAN

Filiz B. Dilek Middle East Technical University

Dept. of Environmental EngineeringAnkara, Turkey

Industrial Waste & Wastewater Treatment & Valorization

May 21-23, 2015 Athens

Biocide!to preserve materials including food, to decontaminate

surfaces, for personal hygiene...

• CAS Number: 3380-34-5• Partition coefficient (Octanol/Water); log KOW = 4.76• Molecular weight = 289.54 g/mol• Density = 1.55 ± 0.04 g/cm3

• Solubility in water = 1 mg/L @ 20°C• Vapor Pressure = 4 x 10-6 mmHg at 20°C

Triclosan (TCS) …

May 21-23, 2015 Athens

• Produced since 1965

• Production of 10-1000 tones per year only in Europe

• Consumption changes from country to country with a total 450tones/yr

Production and use around the world …

May 21-23, 2015 Athens

It is everywhere …

Presenter
Presentation Notes

May 21-23, 2015 Athens

Not hazardous to humans, but skin, eye and respiratory irritations, allergy susceptibility and inhalation toxicityMight be harmful to the immune system Alters hormone regulation in animals-Endocrine distruptioneffects! Toxicity on biota

Bioaccumulation due to its hydrophobic nature –

BCF: 3700-8400 for fish speciesMight contribute to the development of antibiotic-resistant germs

http://www.mayoclinic.org/healthy-lifestyle/adult-health/expert-answers/triclosan/faq-20057861http://www.fda.gov/forconsumers/consumerupdates/ucm205999.htm

Adverse Effects?

May 21-23, 2015 Athens

• Exposure to low levels of TCS disrupts thyroid hormoneassociated gene expression and can alter the rate of thyroid hormone-mediated postembryonic anuran development.

May 21-23, 2015 Athens

Not hazardous to humans, but skin, eye and respiratory irritations, allergy susceptibility and inhalation toxicityMight be harmful to the immune systemAlters hormone regulation in animals-Endocrine distruptioneffects!Toxicity on biota

Bioaccumulation due to its hydrophobic nature –

BCF: 3700-8400 for fish speciesMight contribute to the development of antibiotic-resistant germs

http://www.mayoclinic.org/healthy-lifestyle/adult-health/expert-answers/triclosan/faq-20057861http://www.fda.gov/forconsumers/consumerupdates/ucm205999.htm

Adverse Effects?

May 21-23, 2015 Athens

TCS affected both bacterial and algal communities within the biofilm, although TCS toxicity was higher for bacteria than algae (NEC: 0.21 µg/L for bacteria; 0.42 µg/L for algae).

The potential environmental risk of TCS is high especially in rivers where water scarcity results in low dilution capacity, like in Mediterranean areas.

May 21-23, 2015 Athens

Not hazardous to humans, but skin, eye and respiratory irritations, allergy susceptibility and inhalation toxicityMight be harmful to the immune system Alters hormone regulation in animals-Endocrine distruptioneffects! Toxicity on biota

Bioaccumulation due to its hydrophobic nature –

BCF: 3700-8400 for fish speciesMight contribute to the development of antibiotic-resistant germs

http://www.mayoclinic.org/healthy-lifestyle/adult-health/expert-answers/triclosan/faq-20057861http://www.fda.gov/forconsumers/consumerupdates/ucm205999.htm

Adverse Effects?

May 21-23, 2015 Athens

TCS could exert a selective pressure able to drive the spread of a resistance determinant in a human pathogen – Biocide resistance

However,

No statistical correlation between reduced susceptibility to TCS and any antibiotic resistance!

EC project KBBE-227258 BIOHYPO (2013), which is a research project aimed at evaluating the impact of biocide use on the generation of antibiotic resistance

May 21-23, 2015 Athens

Legislative Acts

• Directive 76/768/EEC (Annex VI)

Maximum authorized concentration: 0.3% in cosmetic products !

• Directives 98/8/EC (528/2012), 95/2/EC and Regulation (EC)1831/2003

Not allowed to be used as disinfectant and preservative in foodand feed production !

Country Level Acts

• Germany introduced a ban on the use of TCS within the plasticproducts having a direct contact with foods since September 2009.

Restriction on use …

May 21-23, 2015 Athens

TCS(ng/L) (µg/kg)*

Surface waters 0.16-2300 BIOHYPO, 2012

Kolpin et al., 2002 Mezcua et al., 2004

Svensson, 2002 Ying -Kookana, 2007

etc.

Marine waters 16.2-99.3

WWTP influent <0.87-562000

WWTP effluent 100-269000

WWTP sludge 28-37189 *

TCS accumulates in sludge !

Environmental Occurence …

May 21-23, 2015 Athens

Adsorption to ozonation system

TCS decrease in identical reactors after 5 h – But, adsorption on glass reactor surface was negligable

0

1

2

3

4

5

6

0 1 2 3 4 5 6TC

S C

once

ntra

tion

(mg/

L)

Time (h)

Glass tubing

Plastic tubing

TCS concentration in glass reactors aerated with plastic or glass tubing (TCS spiked at 5 mg/L)

(without ozone gas, but air)

For ozonation tests, it is definitely advised to use glass reactors with glass tubing if possible

May 21-23, 2015 Athens

Adsorption to membrane filtration system

0100200300400500600700800

0 20 40 60 80 100 120 140TCS

conc

entra

tion

(µg/

L)

Time (h)

0

200

400

600

800

1000

0 20 40 60 80 100 120 140TCS

conc

entra

tion

(µg/

L)

Time (h)

0

200

400

600

800

1000

1200

1400

0 20 40 60 80 100 120 140TCS

conc

netra

tion

(µg/

L)

Time (h)

(NF system - without membrane)

It is essential firstly to saturate the system with TCS without membrane and then to carry out actual runs.

747 µg/L TCS

898 µg/L TCS

1268 µg/L TCS

May 21-23, 2015 Athens

REMOVAL OF TCS FROM WASTEWATER

BIOLOGICAL TREATMENT

Effect of Culture Acclimation on the Fate of Triclosan During Biological Wastewater Treatment

May 21-23, 2015 Athens

Acclimated cultureInfluent TCS

Concentration COD Removal (%)

0 94.0

100 ng/L 93.0

100 µg/L 92.6

500 µg/L 91.0

1 mg/L 84.4

10 mg/L 81.2

20 mg/L 67.6

50 mg/L 57.8

100 mg/L 47.4 TCS > 100 mg/L toxic effects! Positive effect of acclimation !

Influent TCS

Concentration (mg/L)

COD Removal

(%)

0 94.0

1 66.0

10 62.8

20 58.4

50 57.2

100 42.2

Non- acclimated culture

Pulse-fed sequencing batch reactor

May 21-23, 2015 Athens

Acclimated culture Non-acclimated culture

Main TCS removal mechanism: Biodegradation for acclimated Adsorption becomes more prominent for non-acclimated

0.00.10.20.30.40.50.60.70.80.91.0

2 20 40 100 200

Dis

trib

utio

n

Influent TCS as Mass (mg)

TCS Biodegraded

TCS in Effluent

TCS in Sludge

Pulse-fed sequencing batch reactor

May 21-23, 2015 Athens

By-product formation

Parent compound: TCS

BP2: 2,4-DCABP1: 2,4-DCP

Pulse-fed sequencing batch reactor

May 21-23, 2015 Athens

By-product formation

e.g. Non-acclimated culture-10 mg/L TCS (effluent water)

2,4-DCA has not been reported before.Me-TCS was not detected in both culture cases (owing to TCS stock solution prepared in NaOH)

So, one should be very careful in reporting Me-TCS as a by-product of TCS degradation without considering this fact

Acclimation resulted in lower by-product levels

Pulse-fed sequencing batch reactor

May 21-23, 2015 Athens

In the presence of biodegradable COD

Acclimated culture Non-acclimated culture

Reduced COD removal efficiency with higher TCS input ! TCS did not interfere with biodegradable COD use as long as < 20 mg/L !

0.0

0.2

0.4

0.6

0.8

1.0

0 5 10 15 20 25

CO

D/C

OD

o

Time (h)

1 mg/L TCS 10 mg/L TCS

20 mg/L TCS 50 mg/L TCS

100 mg/L TCS

0.0

0.2

0.4

0.6

0.8

1.0

0 5 10 15 20 25

CO

D/C

OD

oTime (h)

1 mg/L TCS 10 mg/L TCS

20 mg/L TCS 50 mg/L TCS

100 mg/L TCS

Kinetics

May 21-23, 2015 Athens

Acclimated culture Non-acclimated culture

Substrate inhibition for non-acclim. culture Reduced inhibition for acclim. culture and substrate inhibition was in approach to the

Monod Model !

0.000

0.002

0.004

0.006

0.008

0.010

0.012

0.014

0.016

0 20 40 60 80 100

µ (1

/h)

TCS (mg/L)

0.000

0.002

0.004

0.006

0.008

0.010

0.012

0 20 40 60 80 100

µ (1

/h)

TCS (mg/L)

In the absence of biodegradable COD

Kinetics

May 21-23, 2015 Athens

REMOVAL OF TRICLOSAN FROM SURFACE WATERS

OZONATIONNANOFILTRATION

Ankara

Kesikköprü Dam

May 21-23, 2015 Athens

TCS levels in surface waters: 0.65–48.96 ng/LTCS levels in the distribution network: below LOQ

May 21-23, 2015 Athens

Ozonation

May 21-23, 2015 Athens

0102030405060708090100

0

50

100

150

200

250

300

350

400

5 10 15 24 70

TC

S re

mov

al (%

)

App

lied

ozon

e (m

g)

Ozone dose (mg/L)

10 min 5 min 1 min 10 min 5 min 1 minOzonation time (for mg) Ozonation time (for %)

about 99% TCS removal in 10 min5 min ozone : almost complete abatement (except 5 mg/L)

Effect of Ozone Dose

May 21-23, 2015 Athens

initial TCS: 1 mg/L, ozone dose: 5 mg/L

t=0

t=10

t=5

t=20 t=30

OH

OH

Cl

Cl

Cl

OH

Undefined t=1

2,4-DCP & 4-CC comply with Chen et al. ( 2012)

Ozonation by-products of TCS

May 21-23, 2015 Athens

Therefore, in ozonation studies being worked with any methyl containingsolutions or solvents, this issue should be considered cautiously.

with methanol

with NaOH

2,4-DCA is formed in the presence of methanol in water.

May 21-23, 2015 Athens

Proposed reaction pathway for ozonation of TCS

May 21-23, 2015 Athens

• Although almost complete TCS depletion in 10 min, ozoneconsumption continued due to the presence of its ozonationby-products (i.e. 2,4-DCP, 4-CC, 2,4-DCA)

Time (min)

O3 consumed/TCS (mg/mg)

Removal

(%)1 2.311 96.05 4.036 98.5

10 6.390 10020 9.841 10030 13.036 100

For complete removal!

Ozone Demand of TCS

May 21-23, 2015 Athens

Membrane used

Membrane Name Polymer Structure pH Range Rejection Size Typical Flux/psi GFD@PSI

DL-NF Thin Film 2-11 96 -MgSO4 31/100

Nanofiltration

May 21-23, 2015 Athens

Surface water spiked with 5000 ppb TCS (TMP:6.9 bar; CFV: 1.2 m/sec)

May 21-23, 2015 Athens

TCS removal from surface water spiked with 5000 ppb TCS

PhaseSystem Sorption Nanofiltration

TCS Concentration (ppb)Initial feed 4626 1862Steady-state feed 1862 1160Steady-state permeate NA 798

TCS Removal (%)Total 60.1 57.1By membrane sorption NA 37.7 (66)By surface rejection NA 19.4 (34)

May 21-23, 2015 Athens

TCS= 2000 ppb, HA: 10 mg C/L;

TCS= 5000 ppb, HA: 10 mg C/L;

TCS= 5000 ppb, HA: 26 mg C/L)

TMP:6.9 bar; CFV: 1.2 m/sec

Effect of HumicAcid (HA) as NOM

HA injected

May 21-23, 2015 Athens

Schematic of processes controlling the permeation of small organics

E. Steinle-Darlinga, M. Zeddab, M. H. Plumleea, H.F. Ridgwaya, M. Reinharda, Evaluating the impacts of membrane type, coating, fouling, chemical properties and water chemistry on reverse osmosis rejection of seven nitrosoalklyamines, including NDMA, Water Res. 41 (2007) 3959 – 3967

May 21-23, 2015 Athens

Effect of HA concentration on TCS retention (TCS:5000 ppb)

NOM had a positive effect on TCS removal (due to TCS-HA complex formation)NOM leads to an increase in TCS removal mainly by sorption into the membrane

May 21-23, 2015 Athens

Effect of HA concentration on flux and flux decline (TCS:5000 ppb)

Positive effect of HA on membrane fouling!Concentration polarization disappeared with anincrease in HA

May 21-23, 2015 Athens

• Significant TCS removal in ASP• Acclimation has a positive effect• By-products of 2,4-DCP and 2,4-DCA, but with lower levels with

acclimation

Remarks- wastewater

May 21-23, 2015 Athens

Ozonation:

• Very effective

• By-products of 4-CC, 2,4-DCP and 2,4-DCA

NF:

• NOM content is a factor in TCS removal from surface water by NF

• TCS removal increases with NOM

Remarks – surface water

May 21-23, 2015 Athens

Supported by EC project KBBE-227258 BIOHYPO and the Scientific and Technological Research Council of Turkey

(TUBITAK–1112Y210) project

Dr. Ulku Yetisand

Dr. Levent Yılmaz, Dr. Erkan Sahinkaya, Aybala K.Orhon, K. Berk Orhon, Abdullah Oğutverici

THANKS...