techniques for measuring ammonia emissions from land applications of manure and fertiliser
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NADP Ammonia Workshop, Washington DC, 22-24 October 2003. Techniques for measuring ammonia emissions from land applications of manure and fertiliser. Tom Misselbrook and Fiona Nicholson. Institute of Grassland and Environmental Research, North Wyke. Structure of presentation. - PowerPoint PPT PresentationTRANSCRIPT
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Techniques for measuring ammonia emissions from land applications of manure and fertiliser
Institute of Grassland and Environmental Research, North Wyke
Tom Misselbrook and Fiona Nicholson
NADP Ammonia Workshop, Washington DC, 22-24 October 2003
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Structure of presentation
Techniques available
• Micrometeorological
• Enclosure
Samplers for measuring concentration (or flux)
Most commonly-used methodologies
• Micrometeorological mass balance
• Wind tunnels
• Equilibrium concentration technique
Conclusions
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Techniques available
• Soil N balance, 15N
Micrometeorological techniques
Mass balance
Eddy correlation
Gradient methods
Backward Lagrangian stochastic model
Equilibrium concentration technique
Enclosure techniques
Static chambers
Dynamic chambers
Controlled release ratio techniques
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Micrometeorological techniques
Mass balance – Integrated Horizontal Flux
upwind mast
downwind mast
winddirection
manure-treated surface
horizontalNH3 flux
verticalNH3 flux
Flux from treated area = (IHFdw - IHFuw) / x
x
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Micrometeorological Mass Balance (IHF) technique
Passive flux samplers mounted on a mast
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Micrometeorological techniques
Mass balance – other methods
Theoretical profile shape – measure flux at 1 predetermined height (Zinst)
TPS Philip’s solution – flux derived from measured concentration profile and theoretically calculated concentration profile for unit flux
Perimeter profile method – measure inward and outward fluxes at several heights around the perimeter of a treated circular plot
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Micrometeorological techniques
Eddy correlation
'' Flux ww’ – fluctuation in vertical wind speed
(sonic anemometer)
x’ - deviation from mean concentration
(TDL)
Relaxed eddy accumulation
wbFlux b – empirical constant
w–standard deviation in vertical wind
x+ - mean concentration, updraft
x- - mean concentration, downdraft
Sonic anemometer
Wet chemistry (e.g. denuder)
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Micrometeorological techniques
Gradient methods
Measure concentration, wind speed and temperature at 2 or more heights
Constant flux layer
Flux = K dX/dz
fetch:height 100:1
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Micrometeorological techniques
Backward Lagrangian stochastic model
u is windspeed,
c is ammonia concentration
n is a constant
Flux = uc/n
Software commercially available
At it’s simplest, requires measurement of windspeed and concentration at only 1 height
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Equilibrium concentration technique
Flux = (Ceq - Ca,z) Kz,a
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Enclosure techniques
Static chambers
Time
Concentration
0
2
4
6
8
10
12
0 2 4 6 8 10
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Enclosure techniques
Dynamic chambers – wind tunnels
Flux = V (Cout - Cin) / A
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Controlled Release Ratio technique
Fluxp = f (Cp - Cb)
where f = Fluxs/(Cs-Cb)
Cp
CbCs
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Samplers
• Laser/optical instruments - TDL, DOAS, FTIR
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Laser/optical Instruments
Advantages:
• very sensitive
• fast response (real-time results)
Disadvantages:
• cost
• require power
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Samplers
• Optical absorption samplers - TDL, DOAS, FTIR
• Absorption flasks
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Advantages:
• inexpensive
• simple
• can be used for a wide concentration range
Disadvantages:
• require power
• time-averaged concentration measurements
• freezing/evaporation problems
Absorption flasks
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Samplers
• Optical absorption samplers - TDL, DOAS, FTIR
• Absorption flasks
• Denuders
• Filters/badges
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Advantages:
• inexpensive
• simple
• no power requirement
Disadvantages:
• labour intensive
• time-averaged concentration measurements
• difficulty in estimating required exposure times
Filters/badges
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Samplers
• Optical absorption samplers - TDL, DOAS, FTIR
• Absorption flasks
• Denuders
• Filters/badges
• Passive flux samplers
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Passive flux samplers – “shuttles”
Advantages:
• direct measurement of flux
• no power requirement
• simple
Disadvantages:
• cost? ($300-400 each)
• time-averaged flux measurement
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Sampler inter-comparison tests
Concentration range 80 – 7,500 ug N m-3
Exposure time 1 – 6 hours
• Absorption flasks – 2 in series
acid concentration (0.1, 0.01, 0.001M)
air flow rate (0.6 – 3.5 l min-1)
end type (scintered glass, open)
• Badges
• Shuttles
angle if incidence of air flow (20o, 40o)
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Sampler inter-comparison tests
Absorption flasks
Mean capture in 1st flask 97%
No sig. effect of acid strength
No sig. effect of air flow rate
No sig. effect of end type
Shuttles
No sig. effect of angle of incidence
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Sampler inter-comparison tests
y = 1.13x + 38.94
R2 = 0.92
0
1000
2000
3000
4000
5000
0 1000 2000 3000 4000
Absorption flasks
Sh
utt
les
Shuttles vs. absorption flasks
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Sampler inter-comparison tests
Badge vs. absorption flasks
y = 1.77x - 583.08
R2 = 0.91
0
2000
4000
6000
8000
10000
12000
0 1000 2000 3000 4000 5000 6000 7000 8000
Absorption flasks
PD
S
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Sampler inter-comparison tests
Sampler repeatability
Sampler CV (%) No. samplersper test
No. tests
Absorptionflask
21 3 or 6 40
Shuttle 10 2 6
Badge 14 4 6
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Sampler inter-comparison tests
‘Blank’ values and detection limits (ug N)
Sampler Mean ‘blank’value
n Detectionlimit
Maximumcollected
Absorptionflask
7.1 56 70 1130
Shuttle 12.7 18 48 770
Badge 1.0 24 2.5 260
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Technique inter-comparisons
ECT
Wind tunnels
MB IHF
Circular manure-treated plot
3 replicate plots
4 experiments (different manure types)
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Technique inter-comparisons
0
2
4
6
8
10
12
Slurry FYM Poultrymanure
Poultrymanure(w etted)
Am
mo
nia
vo
lati
lisat
ion
rat
e (k
g/h
a/h
r) o
n d
ay 1
Mass balancemicrometeorologoy - IHFWind tunnels
Equilibrium concentration
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Technique inter-comparisons
Technique Cattle slurry
Cattle FYM
Poultry (dry)
Poultry (wet)
IHF 23 24 37 52
Wind tunnels
46 84 74 61
ECT * 30 37 39 36
* many missing data
Coefficients of variation (%) in measured emission rates
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Choice of technique
IHF Wind tunnelsECT
type of study absolute comparativecomparative
ease of replication * ******
land area required *** * *
capital cost * *** *
labour costs * ** ***
practicality * * **
variability ** ** **
overall reliability *** ** ** low, ** medium, *** high
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Conclusions
• Large number of techniques available
• Overall methodology
• Sampling concentration/flux
• CV of measurement techniques lowest for MB-IHF
• CV of measurements lower for slurries than solid manures
• Choice of technique depends on purpose and resources available
• Still room for the development of a non-intrusive small plot technique