MARKET - REGULATIONS
Mercury Reduction Status and Programs around the World
The U.S., with less than 5 percent of mercury emissions, is leading the way and 
setting reduction examples for the rest of the world. 
Approximately 2,000 tons of mercury are emitted yearly due to human 
activities. Much of this, in vapor form, travels from continent to continent. So 
it is a worldwide problem.
The present emissions reflect big reductions both intentional and accidental. 
Coal-fired power plants in China have installed SO2 scrubbers and are 
capturing at least 30 percent of the mercury previously emitted. Most European 
countries require scrubbers for SO2 and SCR for NOx. There 
is no mercury limit but the scrubber/SCR combination removes much of the 
mercury.  As a result, coal burning 
worldwide now accounts for only 600 tons of mercury emissions per year as 
opposed to gold mining which is 25 percent greater.
| 
		
		
		Mercury Emissions from Human Activities 
		 (tons per year) | |||
| 
		
		
		Source | 
		
		
		World | 
		
		
		U.S. | 
		
		
		East Asia | 
| 
		
		Municipal Incinerators | 
		
		50 | 
		
		2 | 
		
		20 | 
| 
		
		Cement | 
		
		150 | 
		
		15 | 
		
		150 | 
| 
		
		Coal Burning | 
		
		600 | 
		
		40 | 
		
		300 | 
| 
		
		Mining | 
		
		800 | 
		
		1 | 
		
		300 | 
| 
		
		World | 
		
		2,000 | 
		
		100 | 
		
		800 | 
Most of the world’s waste incinerators have some form of mercury control, so 
actual emissions are approximately 50 tons per year. More than 100 tons is 
captured by pollution control devices.
The U.S. has tough regulations which require compliance over the next three 
years. They affect coal-fired power plants, cement plants, and industrial 
boilers. The regulations are based on mercury weight limits per unit of energy 
consumed or produced.  Regulations 
elsewhere are based on weight per unit of stack gas discharged.
 By taking the details for an average 
plant one calculates the required limit for existing U.S. coal-fired power 
plants at 1.7 ug/m3 to 4 ug/m3.
| 
			
			
			Emission Limits in ug/m3 | ||||
| 
			
			
			Country | 
			
			
			Coal - New Plants | 
			
			
			Coal - Existing Plants | 
			
			
			Incinerators | 
			
			
			Cement | 
| 
			
			U.S. | 
			
			>1 | 
			
			1.7-4 | 
			
			9.5 ( med waste) | 
			
			5 (new) 
			
			12 (existing | 
| 
			
			EU | 
			 | 
			 | 
			
			30 | 
			 | 
| 
			
			Germany | 
			
			30 | 
			
			30 | 
			
			30 | 
			 | 
| 
			
			China | 
			
			30 | 
			
			30 | 
			 | 
			 | 
So the U.S. has set limits which are an order of magnitude lower than other 
countries. But there are local rules and pending rules which are equally 
stringent.
In Germany power plants burning sewage sludge as well as coal must meet the 30 
ug/m3 but one plant is facing a local regulation of 3 ug/m3. 
One coal-fired power plant in the Netherlands is facing a 2.4 ug/m3 
limit. The China Council for International Cooperation has recommended that the 
limit for coal-fired power plants be reduced from 30 ug/m3 to 5 ug/m3 
by 2015 and to 3 ug/m3 by 2020.
The coal-fired power plants in China and Germany need some level of mercury 
reduction to meet the 30 ug/m3 requirement. Typically the particulate 
collector and scrubber combination will provide adequate capture. However, 
mercury levels in the raw coal vary. This means that measurement is necessary 
and in some cases additional controls will be required.
At this point there are stringent requirements for mercury control from waste 
incinerators  in most countries. 
Cement plants, industrial boilers, and utility boilers in the U.S. also now have 
stringent requirements. The reduction solution varies somewhat from industry to 
industry but in general, all the same options are available. Decisions are 
complicated by the fact that mercury removal takes place along with the capture 
of other pollutants. So all the factors listed below need to be considered:
a.      
Process
                               
i.           
Particulate Type
1.     
Electrostatic Precipitator-dry
2.     
Electrostatic Precipitator-wet
3.     
Fabric Filter
                             
ii.           
FGD Process
1.     
Wet limestone
2.     
Spray dryer 
3.     
Circulating dry scrubber
4.     
Dry sorbent injection
                           
iii.           
Capture Mechanism
1.     
Bromine
2.     
Chlorine
3.     
Activated carbon
4.     
Non carbon sorbent
5.     
Membrane
6.     
Gold amalgamation
                           
iv.           
Selection Criteria
1.     
Efficiency 
2.     
Performance
3.     
Maintenance
4.     
Cost
b.     
Process Components
                               
i.           
Capture device in conjunction with particulate device or scrubber
1.     
Activated carbon injection systems
2.     
Halogen slurry injection systems
3.     
Liquid bromine injection
4.     
Advanced SCR catalyst
5.     
Post scrubber membrane
                             
ii.           
Monitoring
1.     
Continuous emissions monitor
2.     
Sorbent trap
                           
iii.           
Re-emissions Prevention
1.     
Chemicals
2.     
Activated carbon
                           
iv.           
Wastewater Treatment
1.     
Physical-chemical
2.     
Biological
3.     
Zero liquid discharge
a.      
Thermal evaporation
b.     
Pressure evaporation
c.      
Flue gas drying
d.     
Sidestream spray drier
Ten years ago when U.S. EPA started its investigation process it appeared that 
activated carbon injection was the best solution across the board. It now is 
apparent that there are many options which should be considered. McIlvaine has 
created a free website to help polluters around the world make the best 
decisions for their plant.
Mercury Removal - Continuous Analyses