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1
Practical Odour assessment
Nigel Gibson
Odour - the problem
The process of concern
Local residents
2
Topics covered
• Complaints• Off-site survey• Odour/odorant sampling• Odour/odorant measurement• Odour assessment
Objectives of odour monitoring
• Establish whether nuisance exists• Enable mitigation program to be defined
3
Complaints
• Sign of problems with a plant or process• Level of complaints may not represent the
true feeling of the community• Complaint level will vary with time
Factors affecting human response
• Physiological factors - age, sex, health...• Social factors - custom, habit, attitude to
source, past experiences...• Meteorological - temperature, humidity...• Local politics
4
Example site - year 1
complants year 1
09/01/98
23/01/98
06/02/98
20/02/98
06/03/98
20/03/98
03/04/98
17/04/98
01/05/98
15/05/98
29/05/98
12/06/98
26/06/98
10/07/98
24/07/98
07/08/98
21/08/98
04/09/98
18/09/98
02/10/98
16/10/98
30/10/98
13/11/98
27/11/98
date
co
mp
lain
t d
ay
s
complants
Example site - year 2
complaints
20/0
1/99
03/0
2/99
17/0
2/99
03/0
3/99
17/0
3/99
31/0
3/99
14/0
4/99
28/0
4/99
12/0
5/99
26/0
5/99
09/0
6/99
23/0
6/99
07/0
7/99
21/0
7/99
04/0
8/99
18/0
8/99
01/0
9/99
15/0
9/99
29/0
9/99
13/1
0/99
27/1
0/99
10/1
1/99
24/1
1/99
08/1
2/99
month
co
mp
lain
t d
ay
complaints
5
Figure 4 odour control parameters v complaints
0
5
10
15
20
25
30
35
40
45
21/05/98 26/05/98 31/05/98 05/06/98 10/06/98 15/06/98 20/06/98 25/06/98 30/06/98
day
be
d te
mp
. (d
eg
C)
0
1
2
3
4
5
6
7
8
9
10
pH
bed temperature
complaints
mex temp
bed pH
acidic pH
Odour Control Parameters v Complaints
Figure1 showing wind speed, direction and complaints in June 1998
0.0
90.0
180.0
270.0
360.0
3600
3624
3648
3670
3694
3718
3742
3766
3790
3814
3838
3862
3886
3910
3934
3958
3982
4006
4030
4054
4078
4102
4126
4150
4174
4198
4222
4246
4270
4294
4318
4342
4366
Hour
Win
d d
ire
cti
on
(d
eg
ree
s f
rom
no
rth
)
0.0
2.0
4.0
6.0
8.0
10.0
12.0
14.0
win
ds
pe
ed
(m
/s)
winddirection
complaints
WIND SPEED
Wind Speed Direction and Complaints in June 1998
6
Community based techniques
• Diaries:• useful, especially if the event is short-term, and out of
hours• some discretion in assessing usefulness. (Validation
by complaints?)• Care needed to interpret diaries (some exaggeration
possible, Validation by complaints?)
• Community surveys:• Expensive if done well• Ideally large population base require• Can differentiate between sources.
Boundary fence/off-site survey 1
Many authorisations contain:
• general odour condition “ ……..no offensive odour……………. as perceived by the local authority inspector”
• routine boundary monitoring by operator
7
Boundary fence/off-site survey 2
Advantages:• cheap• easy (?)Disadvantages:• positive results only under extremes
conditions• discrete test• are the results believed?• observer fatigue
Off-site survey method 1
Method proposed in guidance to WML regulators (EA website) based on assessment of:
Intensity + Extent + Sensitivity of Location
8
Off-site survey method 2
Intensity1. No detectable odour2. Faint odour (barely detectable, need to stand still and
inhale facing into the wind)3. Moderate odour (odour easily detected while walking
and breathing normally, possibly offensive)4. Strong odour (bearable, but offensive odour - will my
clothes/hair smell?)5. Very strong odour (this is when you really wish you
were somewhere else)
Off-site survey method 3
Extent (assuming odour detectable, if not then 0)
1. Local and impersistent (only detected during brief periods when wind drops or blows)
2. Impersistent as above, but detected away from site boundary
3. Persistent, but fairly localised4. Persistent and pervasive up to 50 m from site
boundary5. Persistent and widespread (odour detected >50 m
from site boundary)
9
Off-site survey method 4
Sensitivity of Location where Odour Detected (assuming detectable, if not then 0)
1. Remote (no housing, commercial/industrial premises or public area within 500 m)
2. Low sensitivity (no housing, etc. within 100 m of area affected by odour)
3. Moderate sensitivity (housing, etc. within 100 m of area affected by odour)
4. High sensitivity (housing, etc. within area affected by odour)
5. Extra sensitive (complaints arising from residents within area affected by odour)
Sampling
• Point sources• Open surfaces - with gas flow• Open surfaces - without gas flow
10
Point sources
Open surfaces - with gas flow
11
Open surfaces - without gas flow
Open surfaces - without gas flow
12
Odour measurement/quanitification
• Compound specific techniques• Complex chemical analysis• Olfactometry
Compound specific techniques
• Specific odorants e.g. NH3, RNH2, H2S, RHS
• Marker compounds H2S, methane etc.
Not necessarily a direct correlation with odour
13
Marker compounds- landfill
Marker compounds- STW
14
Marker compounds- brickworks
Figure 1 Odour and H2S concentrations throughout one kiln cycle
0.E+00
5.E+05
1.E+06
2.E+06
2.E+06
3.E+06
3.E+06
4.E+06
4.E+06
5.E+06
5.E+06
6:18
7:20
8:15
9:14
10:1
3
11:1
3
12:1
4
13:1
4
14:1
6
15:1
6
16:1
5
17:1
7
18:1
6
19:1
5
20:1
7
21:1
5
time
Od
ou
r c
on
ce
ntr
ati
on
(o
u/m
3)
0
0.5
1
1.5
2
2.5
3
3.5
time
H2
S c
on
ce
ntr
ati
on
(p
pm
)
tot odour
tot h2s
Complex chemical analysis
Adsorption followed by GC-FID or GC-MS‘Electronic nose’
15
Chemical analysis - GC
Gas chromatography is a widely used analytical technique for characterising odour emissions
Advantages:• Provides quantitative analysis for a broad
range of chemicals
Chemical analysis - GC
Disadvantages
• Does not detect inorganic species, e.g. ammonia & hydrogen sulphide
• Poor detection of highly reactive species• Time resolution of passive sampling is poor
16
Chemical analysis - GC
Chemical Analysis (3)
• Does not take into account additive effects, e.g.
Compensation IabIa+Ib
17
Electronic nose 1
Electronic sensors work in 1 of 2 ways:
Chemical reaction:- responds to the products (or starting materials) of reaction
Micro-environmentally sensitive:- functions by reaction changes occurring in electrical properties. Mixture not substance specific
Electronic nose 2
In the future the electronic nose may offer a practical solution for objectively assessing odours.
Unlike gas chromatography the electronic nose measures all components in a mixture at any one time.
18
Electronic nose 3
Olfactometry 1
It involves the step-wise dilution of a sample of odour-free air and subsequent presentation to a panel of observers in order to determine the number of dilutions required for odour to be perceived by 50% of the members of the panel.
19
Olfactometry 2
1 odour unit =
The amount of odorant(s) that, when evaporated into 1 cubic metre of odourless gas at STP, causes a physiological response from a panel (detection threshold) equivalent to that elicited by 40ppb (0.123mg/m3) of n-butanol
Source: CEN TC264/WG2
Olfactometry 3
20
Olfactometry 4
Olfactometry 5
% Negative response50%10 000
100 000
2
4
3
56789
45 000
Log
10(D
ilutio
n)
Log10 (Dilution) Vs % Negative response
21
Impact assessment overview
Screening or detailed modelling?
• Screening èemission factor data, e.g. for pig farming:weaners 6 ou/animal/sdry sow 19.1 ou/animal/sboar 22.6 ou/animal/sèsimple model (dmax)
• Detailed - full measurement (olfactometry) and modelling study (ADMS, AERMOD)
22
Odour assessment criteria
• Two components:èa concentration component, and èa percentage compliance component.
E.g.Odour concentration shall not exceed X OU/m 3 , corrected for the appropriate peak to mean ratio, for more than Z% of the meteorological conditions.
Criteria used in UK
5 ou/m3 as a 98th%ile of 1 hour averages
• set using pre-1995 Dutch data• Dutch correction factor: 1 ouE/m3 =2 GE/m3
therefore criteria should now read:2.5 ou/m3 as a 98th%ile of 1 hour averages
23
Dutch criteria (NER 2000)
Process Target98th%ile
Limit98th%ile
Bakeries 5Breweries 1.5Slaughterhouse 0.55 1.5Meat processing 0.95 2.5Grass drying 2.5Coffee roaster 3.5Animal feed plant 1composting 0.5 1.5wwtw 0.5-3.5
Example output as a 98th%ile
348000.00 348400.00 348800.00 349200.00 349600.00 350000.00461000.00
461200.00
461400.00
461600.00
461800.00
462000.00
462200.00
462400.00
462600.00
462800.00
463000.00
24
Summary
complaints Off-siteassessment
Monitoring Impactassessment
Nuisanceassessment
Yes Yes Possibly Yes
Mitigationprogram
Possibly Possibly Yes Yes