Waste Incineration The British Experience Mass burning and Fluidised Bed Technology - PowerPoint PPT Presentation

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Waste Incineration The British Experience Mass burning and Fluidised Bed Technology

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Air Pollution UK Consequences. About 20,000 people are killed by traffic pollution every year ... From Dore et al. (2003) Introduction What Are 'Dioxins? ... – PowerPoint PPT presentation

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Title: Waste Incineration The British Experience Mass burning and Fluidised Bed Technology


1
CIWM Conference June 2006
Tracking Micropollutants from Cradle to Grave
J Swithenbank, V Sharifi, D Poole, YB Yang, C Ryu
et al SUWIC Sheffield University Waste
Incineration Centre
2
Presentation Overview
  • National Air Standards
  • Pollutant dynamics UK trends
  • Highlight Selected pollutants
  • Conclusions

3
Air Pollution UK Consequences
  • About 20,000 people are killed by traffic
    pollution every year.
  • About 8000 people are dying yearly because of
    particulate matter alone.
  • Life expectancy is increased by 1.5 to 3.5 days
    if
  • 1 µm g/m3 reduction of PM2.5 is achieved.
  • The Guardian, 2003
  • COMEAP (1998)

4
Incinerators meet tighter regulations for NOx
SOx etc than most other combustion systems,but
there is- A UK public perception problem
  • E.g. Dioxins from incinerators are 1 of the UK
    total. Bonfire night on November 5th creates
    more dioxins!

5
UK Legislation
  • Power Station Emissions Covered by the LCPD
    (Large Combustion Plants Directive).
  • Waste Incinerator Emissions Covered by the WID
    (Waste Incineration Directive, 2000/76/EC).
  • Pollutants in the environment would increase if
    an incinerator were to close since the emissions
    from the replacement power station would be
    greater!
  • The Goal posts continue to move.

6
Example of Pollutant Dynamics and Health Effect
7
  • SUWIC Programme Strategic Overview
  • Pollutants from combustion systems
  • Power stations
  • Vehicles
  • Cement kilns
  • Incinerators
  • Micro-pollutants
  • Heavy Metal Emission Measurements
  • Dioxins/Furans/PCBs

8
CO in the UK (2001)
9
CO Spatial Distribution in the UK (2001)
From Dore et al. (2003)
10
NOx Spatial Distribution in the UK (2001)
From Dore et al. (2003)
11
Introduction What Are Dioxins?
  • 210 congeners 75 dioxins and 135 furans
  • 17 toxic congeners with Cl atoms in 2,3,7,8
    positions
  • Toxicity of congeners expressed in TEFs and TEQs
  • 2,3,7,8-TCDD most toxic congener with TEF of 1

12
SUWICs Research in Dioxin REVIEW
? Dioxins/Furans - Solvent extraction unit
- Ion Trap GC-MS/MS (Varian Ltd.
Dionex Ltd.) - Immuno-assay facilities -
Dioxin Research Network
13
Analytical Sampling
14
Analytical Sampling
Bottom ash
Superheater residue
Fabric filter ash
Economiser ash
15
Modelling Approach
Formation in Boiler System
Adsorption in Fabric Filters
16
Modelling Review De Novo Synthesis
  • Dioxins generated at moderate temperatures from
    particulate organic carbon in fly ash by
    gas-solid reactions with O2 and halides.
  • Influencing Factors
  • Temperature 250oC 400oC
  • Carbon of certain degenerated graphitic structure
    is primary source concentration in ash
  • O2 essential
  • Cu (II) ions concentration in ash, strong
    catalytic effect

17
Modelling Formation Rate
18
Modelling Formation Rate
19
The total concentration of PCDD/F formed
20
Modelling Formation Rate for 13 Incinerators
before clean-up filter
21
PCDD/F removal efficiency in fabric filters
22
Modelling Removal Rate
23
Comparison of Predicted vs measured PCDD/F for 11
Incinerators
24
Why 850 deg C for 2 seconds ? It is neither
necessary nor very relevant
25
PCDD/F vs residence time
TAMARA data
26
The Dioxin Research Network www.sheffield.ac.uk/S
UWIC/ - A valuable source of data
27
Fire Smoke is Largely Organic Oils
  • Landfill fire smoke at Tequila, Mexico

28
Particulate Matter
  • Source apportionment is difficult due to
  • 1. Contribution from many different sources.
  • 2. Emissions from some potentially large
    sources are not well established.
  • 3. Variation in atmospheric lifetimes and range
    of travel.

29
One Source of Particulates mass burn of
waste/biomass on a moving bed
30
Recent Bed Modelling Research Progress
  • SUWIC has developed a numerical model of
    combustion in the incinerator bed FLIC
  • Flow channelling, radiation, conduction.

31
Particle random packing theorychannel formation
and gas flow
32
Simulation of gas velocity (m/s) by channel
formation in a packed bed
Grate causes initial uniform flow
33
Particle size emitted along the bed.
34
Emitted Particle Composition along bed length
35
DiagnosticsMeasurement of Heavy Metals in
Gases,Liquidsand Solids
36
On the move
SUWIC Mini-Lab leaves Spectro factory, Kleve,
Germany. 7 February 2002
37
Heavy Metals Continuous Analysis Transportable
Mini-Lab
38
Heavy Metal Measurement
Inductively Coupled Argon Plasma (ICAP) gt
6000K
To Continuous Analysis Spectrometer. Linear over
6 decades
70 Elements Emission Spectrum
39
(No Transcript)
40
Waste incinerator plant, showing the sampling
locations
41
Sodium concentrations for a 4.5 Hour Period,
measured on the 589.592 nm emission line (NB Gaps
in this, and subsequent emission measurements are
due to cleaning of the sample probe to remove
deposited ash).
42
Comparison of sodium and potassium concentrations
for a 4.5 hour period, showing strong correlation
43
Lead concentrations for a 4.5 hour period
measured on the 405.778 nm emission line before
the gas cleaning system.
44
24-Hour Emission Profile for Lead after the gas
cleaning system. (The large spikes correspond to
the injection of standard calibration samples
into the instrument)
0.01mg/m3
45
Cadmium concentrations for a 4.5 hour period,
measured on the 226.503nm wavelength
46
Mercury concentrations for a 6 hour period
measured on the 253.653 nm wavelength before the
gas cleaning system.
47
Conclusions
  • Pollution levels vary significantly with time and
    place, hence pollutant modelling and health
    impact analysis must take account of the
    historical record and anticipated future
    developments.
  • Dioxin emission levels are well controlled and
    mechanisms are largely understood.
  • Advanced numerical modelling of the bed and
    freeboard show particulate emissions vary
    significantly along the incinerator bed.
  • Our unique mobile ICP/OES instrumentation gives
    continuous measurement of more than 50 species
    including all the heavy metals.
  • Sodium and potassium concentrations are closely
    correlated. Observed fluctuations in lead,
    cadmium and mercury are due to changes in plant
    feed.
  • New results from dynamic measurements before and
    after the flue gas clean-up confirm excellent
    process efficiency.
  • Proper facilities for battery disposal are
    urgently needed in the UK
  • Engineering progress has succeeded in ensuring
    that Practically all pollutants born within an
    incinerator reach their grave within the plant.

48
The End
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