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How China Can Leapfrog the World in Mercury Emission Reductions

How China Can Leapfrog the World in Mercury Emission Reductions

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<strong>How</strong> <strong>Ch<strong>in</strong>a</strong> <strong>Can</strong> <strong>Leapfrog</strong><br />

Title of Slide <strong>the</strong> <strong>World</strong> <strong>in</strong><br />

<strong>Mercury</strong> <strong>Emission</strong> <strong>Reductions</strong><br />

Sid Nelson Jr.


Impressive Development Throughout <strong>Ch<strong>in</strong>a</strong>


But Ever-Increas<strong>in</strong>g Pollution


<strong>Mercury</strong> from Power Plants


Ch<strong>in</strong>ese Coals Average ~50% Higher Hg<br />

<strong>Ch<strong>in</strong>a</strong><br />

USA<br />

0.00 0.05 0.10 0.15 0.20<br />

Average coal Hg content, ppm, dry basis.<br />

Various sources. The difference may be even greater.


Overview of <strong>the</strong> <strong>Mercury</strong> Problem<br />

Source: U.S. EPA


Effects Observed <strong>in</strong> Small Newborn Samples<br />

2006 Jedryckowski, et al., “Effects of Prenatal Exposure to <strong>Mercury</strong> on<br />

Cognitive and Psychomotor Function <strong>in</strong> One-Year-Old Infants:<br />

Epidemiologic Cohort Study <strong>in</strong> Poland,” Annals Epidemiology 16:439–447.<br />

2006 Marques, et al., “Maternal mercury exposure and neuro-motor development<br />

<strong>in</strong> breastfed <strong>in</strong>fants from Porto Velho Brazil” Int J Hyg Environ Health, 210(1):51.<br />

2007 Gao, et al., “Prenatal exposure to mercury and neurobehavioral development<br />

of neonates <strong>in</strong> Zhoushan City, <strong>Ch<strong>in</strong>a</strong>,” Environmental Research, 105:390-399.<br />

2007 Suzuki, K., et al., “Associations of neonatal neurobehavioral status with<br />

cord blood PCB, maternal hair mercury, and maternal fish <strong>in</strong>take <strong>in</strong> <strong>the</strong><br />

Tohoku Study Of Child Development ,” Organohalogen Compounds, 69:262.<br />

2007 Xue, et al., “Maternal fish consumption, mercury levels, and risk of<br />

preterm delivery,” Environmental Health Perspectives, 115(1):42. (U.S.)


In <strong>the</strong> U.S., Hg from Fish Lowers IQ<br />

Oken (2005):<br />

• lower<strong>in</strong>g Hg 50% raises IQ = 2 po<strong>in</strong>ts<br />

Oken (2008):<br />

• lower<strong>in</strong>g Hg 50% raises IQ = 1.5 po<strong>in</strong>ts<br />

Lederman (2008):<br />

• lower<strong>in</strong>g Hg 50% raises IQ = 2.5 po<strong>in</strong>ts<br />

Oken, E., et al., “Maternal Fish Consumption, Hair <strong>Mercury</strong>, and Infant Cognition<br />

<strong>in</strong> a U.S. Cohort,” Environmental Health Perspectives, 113(10):1376, 2005.<br />

Oken, E., et al., “Maternal Fish Intake dur<strong>in</strong>g Pregnancy, Blood <strong>Mercury</strong> Levels, and<br />

Child Cognition at Age 3 Years <strong>in</strong> a US Cohort,” Am J Epidemiol 167:1171–1181, 2008.<br />

Lederman, et al., “Relation between Cord Blood <strong>Mercury</strong> Levels and Early Child Development<br />

<strong>in</strong> a <strong>World</strong> Trade Center Cohort,” Environmental Health Perspectives, 116(8):1085, 2008.


Fish MeHg Varies Directly with Deposited Hg<br />

<strong>in</strong> <strong>the</strong> fish<br />

• Isotopically enriched Hg(II)<br />

(90.9% 202 Hg +2 ) was spiked <strong>in</strong>to<br />

large, isolated lake sections<br />

• Uptake monitored <strong>in</strong> zooplankton,<br />

benthic <strong>in</strong>vertebrates, & fish<br />

• “We conclude that concentrations<br />

of spike MeHg <strong>in</strong> <strong>the</strong> food web<br />

of <strong>the</strong> mesocosms were<br />

directly proportional to <strong>the</strong><br />

rates of Hg(II) load<strong>in</strong>g.”<br />

Orihel, et al., “Experimental evidence of a l<strong>in</strong>ear relationship between <strong>in</strong>organic mercury load<strong>in</strong>g<br />

and methylmercury accumulation by aquatic biota,” Environ. Sci. Technol. 41: 4952, 2007.


<strong>How</strong> Is Hg Done <strong>in</strong> <strong>the</strong> U.S.? ACI<br />

B-PAC<br />

H-PAC<br />

C-PAC<br />

Boiler<br />

ESP<br />

/FF<br />

700F 300F<br />

Air Preheater<br />

Fly Ash<br />

Brom<strong>in</strong>ated Powdered Activated Carbon Injection (ACI) before <strong>the</strong> ESP


ACI System<br />

We have <strong>in</strong>stalled<br />

10 systems<br />

Lances stick<strong>in</strong>g<br />

<strong>in</strong>to <strong>the</strong> ductwork<br />

10-cm transport<br />

l<strong>in</strong>e<br />

& sold many millions<br />

of kgs of brom<strong>in</strong>ated<br />

carbons<br />

Silo to hold <strong>the</strong> PAC<br />

& blower(s)<br />

Deliver<strong>in</strong>g<br />

brom<strong>in</strong>ated PAC


Over 100 ACI Systems Sold<br />

<strong>Can</strong> be expensive for 90%<br />

(but “micro-<strong>in</strong>jection” is<br />

not & is suited to plants<br />

without FGD)<br />

55,000 MW<br />

of capacity


Leverage Hg <strong>Reductions</strong> from Scrubbers<br />

<strong>Ch<strong>in</strong>a</strong><br />

USA<br />

0.00 0.20 0.40 0.60 0.80 1.00<br />

Fraction of Power Plants with FGD


Many Ch<strong>in</strong>ese Coals Have Low Halogens<br />

High Cl<br />

Low Cl<br />

USGS prelim<strong>in</strong>ary data on 305 samples<br />

Vosteen, “Ch<strong>in</strong>ese Low Chlor<strong>in</strong>e Coals Need Brom<strong>in</strong>e for<br />

Co-Benefit <strong>Mercury</strong> Capture,” EUEC Conference, 2010.


Oxidize Hg(0) with CaBr 2<br />

on Coal<br />

While wet scrubbers<br />

remove most of <strong>the</strong> Hg+2<br />

from <strong>the</strong> flue gas,<br />

<strong>the</strong>y remove essentially<br />

zero of <strong>the</strong> Hg(0)<br />

Add<strong>in</strong>g a small amount of<br />

bromide to <strong>the</strong> coal can<br />

change Hg(0) to Hg+2 so<br />

<strong>the</strong> scrubber can remove it


Very Simple & Inexpensive<br />

Just drip a CaBr 2 salt solution onto <strong>the</strong> coal


Ch<strong>in</strong>ese Wet Scrubbers<br />

100<br />

Usually ~ 70%<br />

from ESP+FGD;<br />

But sometimes<br />

much less<br />

Guizhou Guizhou Guizhou Guangdong Shanxi Beij<strong>in</strong>g<br />

(SCR)<br />

Wang, et al.,”<strong>Mercury</strong> emission and speciation of coal-fired power plants <strong>in</strong> <strong>Ch<strong>in</strong>a</strong>,”<br />

Atmos. Chem. Phys., 10, 1183–1192, 2010.


Two More<br />

1.00<br />

0.90<br />

This one low<br />

Hg very low<br />

capture<br />

M e rc u ry R e d u c tio n<br />

0.80<br />

0.70<br />

0.60<br />

0.50<br />

0.40<br />

0.30<br />

0.20<br />

0.10<br />

Hebei<br />

Zhang et al., “<strong>Mercury</strong> <strong>Emission</strong>s from<br />

Six Coal-Fired Power Plants <strong>in</strong> <strong>Ch<strong>in</strong>a</strong>’”<br />

Fuel Process<strong>in</strong>g Technology, 1033, 2008.<br />

0.00<br />

No SCR<br />

SCR On<br />

Ozone<br />

Season<br />

Wu, et al., “Evaluation of mercury speciation and<br />

removal through air pollution control devices of a<br />

190 MW boiler,” Environmental Sciences, 227, 2010.


D<br />

Dombrowski (URS) et al., “Near and Long Term Options for Controll<strong>in</strong>g<br />

<strong>Mercury</strong> from Power Plants,” MEGA Symposium, August 2008.


Lum<strong>in</strong>ant Monticello Station<br />

TX Lignite/PRB & LSFO + KNX CaBr2<br />

- CaCl 2 not work, but CaBr 2 did:<br />

30% 85% with ~100 ppm<br />

Benson, EERC, Richardson, URS, et al., “Large-Scale <strong>Mercury</strong> Control Technology Test<strong>in</strong>g for Lignite-Fired Utilities –<br />

Oxidation Systems for Wet FGD,” DOE NETL Hg Control R&D Program Review, 2006.


NRG Energy’s Limestone Station<br />

Coal Blend with Wet Scrubber<br />

Tried CaBr2 with & without PAC<br />

Conditions %Hg Removal<br />

Basel<strong>in</strong>e 30%<br />

0.5 lb/MMacf 50%<br />

100ppm CaBr2 70%<br />

0.5 + 100 ppm 80%<br />

1.6 + 280 ppm 90%<br />

30% 70% with 100 ppm


We Energies’ Pleasant Prairie Plant with SCR<br />

- PRB coal<br />

- SCR<br />

- Wet FGD<br />

- KNX = CaBr2<br />

55% 90%<br />

with 10-20 ppm<br />

R<strong>in</strong>i, et al., “Full-scale Test Results From a 600 MW<br />

PRB-fired Unit Us<strong>in</strong>g Alstom’s KNX Technology<br />

for <strong>Mercury</strong> <strong>Emission</strong>s Control” Air Quality VII, 2009.


Costs Are T<strong>in</strong>y Compared to O<strong>the</strong>r Pollutants<br />

Costs <strong>in</strong> <strong>the</strong> USA<br />

$/kW<br />

SO2: Scrubbers $250<br />

NOx: SCR $150<br />

PM: Fabric Filter $60<br />

Hg: ACI<br />

Hg: CaBr2<br />

$3<br />

$1<br />

• Work underway on United Nations global<br />

legally b<strong>in</strong>d<strong>in</strong>g <strong>in</strong>strument on mercury<br />

• <strong>Ch<strong>in</strong>a</strong> can <strong>in</strong>expensively lead <strong>the</strong> way


Take-Home Messages<br />

1. Every year that <strong>Ch<strong>in</strong>a</strong> delays reduc<strong>in</strong>g Hg, it lower its IQ<br />

2. Brom<strong>in</strong>ated activated carbon <strong>in</strong> <strong>the</strong> U.S., but can be expensive<br />

3. Add<strong>in</strong>g small amounts of CaBr 2 to <strong>the</strong> coal can result <strong>in</strong><br />

significantly improved Hg co-reductions <strong>in</strong> FGD at many plants<br />

4. Very simple, very cheap, and very cost-effective<br />

5. With CaBr 2 on FGD (and micro-<strong>in</strong>jection without FGD), <strong>Ch<strong>in</strong>a</strong><br />

can leapfrog <strong>the</strong> U.S. & <strong>the</strong> world <strong>in</strong> Hg reductions

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