Photocatalytic Roads - ECTRI website/Session 9/YRS11... · DTU, Denmark, 8 – 10 June, 2011...

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Young Researchers Seminar 2011 DTU, Denmark, June 8 - 10, 2011 Young Researchers Seminar 2011 DTU, Denmark, 8 – 10 June, 2011 Photocatalytic Roads From lab tests to real scale applications Dr. Eng. Elia Boonen Belgian Road Research Centre BRRC

Transcript of Photocatalytic Roads - ECTRI website/Session 9/YRS11... · DTU, Denmark, 8 – 10 June, 2011...

Young Researchers Seminar 2011DTU, Denmark, June 8 - 10, 2011

Young Researchers Seminar 2011DTU, Denmark, 8 – 10 June, 2011

Photocatalytic RoadsFrom

lab

tests to real

scale

applications

Dr. Eng. Elia

Boonen

Belgian

Road

Research

Centre

BRRC

2

Contents

Photocatalysis?•

Photocatalytic

concrete

Mechanism

why?▫

Lab

measurements

important parameters

Pilot project

Antwerp

(2004-2005)•

New applications (2010-2011)▫

Prenormative

research

PhotoPAQ

«

Leopold

II tunnel

»▫

ECO2Profit – « Den Hoek 3 »

Conclusions –

perspectives

Photocatalytic

Roads: From lab tests to real scale

applications

3

Photocatalysis?

Photocatalytic

Roads: From lab tests to real scale

applications

CO2 H2 O NO3

-

Pollutants

4

Photocatalytic

concrete: mechanism?

Pollutants UV Radiation

Adsorption and decomposition Photocatalytic Concrete Concrete with TiO2

CTG

Photo: phenomenon induced by (sun) light (UV-spectrum)

Catalyst: a compound which

initiates

a chemical

reaction, without being

used

during

this

reaction

Mostly

in the

form

of

microparticles

of

titanium

dioxide

(TiO2

) in the crystal form anatase

Photocatalytic

Roads: From lab tests to real scale

applications

5

Photocatalytic

concrete: why?

Photocatalytic

Roads: From lab tests to real scale

applications

Important pollutants in trafic

CO : carbon monoxide•

SO2

: sulphur dioxide•

NOx

: nitrogen oxides (NO and NO2

)•

CO2

: carbon dioxide•

PM : particulate matter

VOC : volatile organic compounds•

O3

: ozone (secondary pollutant) •

Pb: lead

Toxicity, smog formation, acid rain,…

6

NOx - nitrogen oxides (NO-NO2 )

Transport sector is responsible for over 50% of NOx

coming from human activity!

Example: Exhaust of NOx

by traffic during rush hour in Paris

Energy industries14%

manufacturing industries and construction

24%transport54%

other energy use6%

other 2%

Photocatalytic

Roads: From lab tests to real scale

applications

7

10.000 m²

of photocatalytic

pavement blocks as pilot project on the parking lanes of a main axe in Antwerp was constructed in 2004-2005

2*4.5m on a total width of 60 m!

First application in Belgium: Sideways of the “Leien” in Antwerp

Photocatalytic

Roads: From lab tests to real scale

applications

8

Pre-treatment: rinsing with distilled water and drying overnight at laboratory conditions

Photocatalytic pavement block

TiO2 containing top layer

Air inlet Air outlet

UV transmitting cover

Air inlet Air outlet

T: 23°C

R.H.: 50%

Air flow: 3 l/min

NO-conc.: 1 ppmV

Light intensity: 10 W/m²

Photocatalytic

concrete: how

to measure?

ISO 22197-1 (2007)

Photocatalytic

Roads: From lab tests to real scale

applications

9

• Semi-conductor TiO2

(anatase

form) at the surface • In the presence of UV-light (300-400nm)

• Contact with pollutants necessary•

Formed NO3

-

is adsorbed at concrete surface (alkalinity) and can

subsequently be washed away by rain

HNOOHNO 2TiO, 2hv

HNOOHNO -3

TiO,2

2hv

Lab tests: removal of NOx

Photocatalytic

Roads: From lab tests to real scale

applications

10

Lab tests: measurement set-up BRRC

Photocatalytic

Roads: From lab tests to real scale

applications

Following ISO 22197-1 (2007)

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Example of measurement according to ISO

Photocatalytic

Roads: From lab tests to real scale

applications

-0,2

0,0

0,2

0,4

0,6

0,8

1,0

1,2

0:00:00 1:12:00 2:24:00 3:36:00 4:48:00 6:00:00 7:12:00

Time

Con

cent

ratio

n (p

pm)

NONO2NOX

5 hours of UV-irradation!

12

Example of short procedure according to BRRC

Photocatalytic

Roads: From lab tests to real scale

applications

0.0

0.2

0.4

0.6

0.8

1.0

1.2

0:00:00 0:07:12 0:14:24 0:21:36 0:28:48 0:36:00 0:43:12

Tijd

Con

cent

ratie

(ppm

)

NONO2NOX

Start UV

Stop UV

Start UV

Stop UV

13

Increase of photocatalytic reaction by:

• Increase of contact time▫

Air flow (l/min)

Turbulence▫

Contact area

Increase of light intensity (UV-light,W/m²)•

Decrease of relative

humidity (RH %)•

Optimum TiO2

-content (efficiency -

durability)

Photocatalytic

Roads: From lab tests to real scale

applications

-25%

-20%

-15%

-10%

-5%

0%

Relative humidity [%]

Red

uctio

n of

NO

x in

flow

with

1 p

pmV

NO

conc

entr

atio

n [%

]

3030 40% 50 60 70

-0,2

0

0,2

0,4

0,6

0,8

1

1,2

0:00:00 0:20:00 0:40:00 1:00:00 1:20:00 1:40:00 2:00:00

Time

conc

(ppm

) NONO2NOx

UV intensity: 1.0 mW/cm²

UV intensity: 0.5 mW/cm²

14

Important for heterogenous photocatalysis:

Acces to light –

light intensity, wavelength•

Acces to pollutants: air flows, contact time, relative humidity

Removal of deposited pollutants: by rain or washing

Photocatalytic

Roads: From lab tests to real scale

applications

15

Pilot project: Leien

in Antwerp

(2004-2005)

Photocatalytic

Roads: From lab tests to real scale

applications

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Results: influence of washing the pavement blocks

Photocatalytic

Roads: From lab tests to real scale

applications

00,10,20,30,40,50,60,70,80,9

9/01

/200

6 (z

.w.)

6/09

/200

6

27/0

8/20

07(z

.w.)

27/0

8/20

07

4/04

/200

5

6/09

/200

6

27/0

7/20

06

27/0

8/20

07(z

.w.)

27/0

8/20

07

9/01

/200

6 (z

.w.)

27/0

7/20

06

9/01

/200

6(z.

w.)

30 35 37 42 48 53

Positioning (nr. Amerikalei)

Min

imum

NO

-con

cent

ratio

n (p

pmV

) m

easu

red

on 2

pav

emen

t blo

cks

30 9/01/2006 (z.w.) 30 6/09/2006 30 27/08/2007 (z.w.) 30 27/08/200735 4/04/2005 35 6/09/2006 37 27/07/2006 37 27/08/2007(z.w.)37 27/08/2007 42 9/01/2006 (z.w.) 48 27/07/2006 53 9/01/2006(z.w.)

17

Results Antwerp 2010

Photocatalytic

Roads: From lab tests to real scale

applications

0

0,1

0,2

0,3

0,4

0,5

0,6

0,7

0,8

0,9

9/09/2010 A 9/09/2010 B 10/10/2010 A 10/10/2010 B 10/10/2010 C

Sample Amerikalei

Min

imum

NO

-con

cent

ratio

n (p

pmV

) m

easu

red

on 2

pav

emen

t blo

cks

=> Durable activity!

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Increasing and decreasing light intensity

0

0,1

0,2

0,3

0,4

0,5

0,6

0,7

0,8

0,9

1

1,1

0:00:00 0:30:00 1:00:00 1:30:00 2:00:00 2:30:00 3:00:00 3:30:00 4:00:00 4:30:00 5:00:00 5:30:00

Time

NO

x-co

ncen

tratio

n at

out

let (

ppm

)

NOSeries2

1000Lux

2000Lux

3000Lux

4000Lux

5000Lux

Stop NO0Lux

New developmentsNew and more efficient materials, also working under visible light:

Photocatalytic

Roads: From lab tests to real scale

applications

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New projects (2010-2013)

“Characterisation of photocatalytic (building) materials”

Prenormative

research (NBN) into

testing

methods

PhotoPAQ

Demonstration

project

within European

Life+-programme

Application in Leopold

II-tunnel

of Brussels

ECO2PROFIT

INTERREG project in cooperation with POM Antwerp (regional development)

Application of photocatalytic

concrete with TiO2

in top layerPhotocatalytic

Roads: From lab tests to real scale

applications

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Photocatalytic concrete: new testing methods•

Prenormative research project CCN/PN/NBN 706: comparative study of test methods within European normalisation actions (CEN/TC386/WG 2)

CTG

21

Photocatalytic concrete: new applications •

LIFE+

project PhotoPAQ: application of cementitious photocatalytic materials on the walls and roof of Leopold II tunnel in Brussels

and

measurement of effect on air pollution inside

Improvement

of air quality

?!

CTG

Cfr. photopaq.ircelyon.univ-lyon1.fr

Pollutants UV Radiation

Adsorption and decompositionPhotocatalytic Concrete

Concrete with TiO2

Photocatalytic

Roads: From lab tests to real scale

applications

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Photocatalytic concrete: new applications (2) •

INTERREG project ECO2PROFIT: application of double layered concrete with recycled concrete aggregates (CO2

)

in the bottom layer and photo- catalytic materials (TiO2

) in the top layer on industrial site “Den Hoek 3” in Wijnegem

(province of Antwerp)

CTGPhotocatalytic

Roads: From lab tests to real scale

applications

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Demonstration project “Den Hoek 3”

Test program to optimize air purifying action in top layer:▫

Testing of different materials

Influence curing compound

Exposed aggregates surface

Simulation of durability

Construction of trial sections

With conservation of other properties (workability, mechanical, frost-thaw,…)

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Fundamental choice for photocatalytic concrete roads:

Exposed aggregates surface:

noise reduction,

comfort

Optimization

of concrete composition

(both layers)

Spraying on the surfaceTiO2

-dispersion:

+ direct action+ cost

(“ordinary”

cement)

-

Durability (adhesion to surface)?

Mixing in the mass TiO2

in cement:

+ durable action-

cost

(higher

concentration

and double layered concrete)-

indirect action

(only the TiO2

at the surface is active)

Demonstration project “Den Hoek 3” (2)

Photocatalytic

Roads: From lab tests to real scale

applications

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W/C = 0.42, Cmin = 425 kg/m³, air content: 5-8%

=> Control consistency, air content, volumetric mass,…

Concrete 0/6,3 (top layer) - Wijnegem

0

10

20

30

40

50

60

70

80

90

1008,06,34,02,01,00,2500,1250,063

Sieve size [mm]

Cum

ulat

ive

mas

s re

tain

ed [%

]

ReferentieOCW volgens berekeningARC

Composition

Material Quantity (kg)

CEM III/A 42.5 N LA 425

Sea sand 0/4 735

Porphyry 4/6,3 973

Air-entraining agent 0,65

Plasticizer 1,5

Water 178,5

Optimization of concrete composition

Photocatalytic

Roads: From lab tests to real scale

applications

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Simultaneous

test plates

with

concrete of

top layer and spraying of photocatalytic dispersion on the surface

20

days conservation

under atmospheric conditions, and subsequent storage at RH

= (60 ±

2)% and

T = (20 ±

2)°C, for

15 days

Zone 1 (with

dispersion)

Zone 2 (without

dispersion)

Construction of trial section

Photocatalytic

Roads: From lab tests to real scale

applications

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=> Substantial and repeatable photocatalytic efficiency

Results for air purifying action of test plates:OCW 7366/5

00,050,1

0,150,2

0,250,3

0,350,4

0,450,5

0,550,6

0,650,7

0,750,8

0,850,9

0,951

1,051,1

0:00

:00

0:02

:00

0:04

:00

0:06

:00

0:08

:00

0:10

:00

0:12

:00

0:14

:00

0:16

:00

0:18

:00

0:20

:00

0:22

:00

0:24

:00

0:26

:00

0:28

:00

0:30

:00

0:32

:00

0:34

:00

0:36

:00

0:38

:00

0:40

:00

0:42

:00

0:44

:00

0:46

:00

0:48

:00

0:50

:00

0:52

:00

0:54

:00

0:56

:00

0:58

:00

1:00

:00

1:02

:00

1:04

:00

1:06

:00

1:08

:00

1:10

:00

1:12

:00

1:14

:00

Time (uu:mm:ss)

Con

cent

ratio

n N

Ox

(ppm

)

NO ppmNOX ppmNO2 ppm

Start UV

Stop UV

Start UV

Stop UV

21.4 ± 1.9NO

11.2 ± 1.0NOx

Average reduction (%)

Photocatalytic

Roads: From lab tests to real scale

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Effect of curing compound

0

5

10

15

20

25

30

35

40

45

50

A B C DPhotocatalytic sample

Red

uctio

n N

Ox

[%]

with curing

without curing

Different products in the mass

0

10

20

30

40

50

60

70

80

90

100

1 2 3Type of TiO2 product

Red

uctio

n N

O, N

Ox

[%]

reduction NO

reduction NOx

Further testing in the lab

Effect of different materials Effect of curing compound

different photocatalytic products (1,2,3) mixed in the mass (no curing compound, modified curing procedure). Curing compound = to protect against desiccation

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Further testing in the lab (2)

Effect of surface treatment Effect of brushing/washing

Only one type of “less active” product in mass

Effect of surface treatment

0

5

10

15

20

25

exposed aggregates smooth, formwork sawnType of surface

Red

uctio

n N

O, N

Ox

[%] reduction NO

reduction NOx

Effect of brushing/washing (durability)

0

5

10

15

20

25

30

35

40

45

50

F D D'Photocatalytic sample

Red

uctio

n N

Ox

[%]

before brushing

after brushing and washing

Simulation of traffic and/or weathering

30

Influence of curing compound▫

Application of photocatalytic dispersion afterwards (2-3 months)

Optimization of concrete composition and choice of photocatalytic materials (in mass + dispersion!)

Effect of exposed aggregates surface finish▫

Active components at surface ↔ specific surface area

Durability of the photocatalytic action (in the lab)

Conclusions test program “Den Hoek 3”

Photocatalytic

Roads: From lab tests to real scale

applications

Final choice “Den Hoek 3” = COMBINATION:•

TiO2 in mass with curing compound & spraying

of photocatalytic dispersion after 3 months •

Provisional controls of photocatalytic efficiency

(in situ & in the lab: 2011-2012)

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Perspectives of

photocatalytic

materials•

Promising results in the lab for NOx

abatement with several photocatalytic

(building) materials

Durability of the air purifying performance was shown, even after more than 6 years in service

Translation of results obtained in laboratory towards results in

situ remains difficult:=> Further need to demonstrate effectiveness in large scale projects, including other positive effects (O3 , VOC’s, PM,…)=> Application of photocatalytic materials is not effective everywhere, e.g. pollution source and wind are very important

Contact and/or more information:Anne Beeldens, [email protected] Boonen, [email protected]

Photocatalytic

Roads: From lab tests to real scale

applications

32Photocatalytic

Roads: From lab tests to real scale

applications

Acknowledgements

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Thank you for your attention!