A review of the odour impact assessment
criteria adopted by other countries indicates that those more commonly used
include a percentile component (varies from 99.5 percentile to 99.9
percentile). This contrasts with
the 100% compliance criteria used in
In order to review the predicted results
for the Extension based on the percentile approach, the highest odour
concentrations predicted at the representative assessment points of TVB City
(A2) and TKO Area 137 (A1-3) are presented in 3-minutes and 1-hour averages and
compared with the odour impact assessment criteria adopted by the overseas
countries. The results are
presented in Annex A12-2 and
summarised in Table A12.1a. As can be seen, the predicted odour
concentrations at TVB City and TKO Area 137 comply with most of the odour
assessment criteria adopted by these countries except the odour criteria
adopted by US for A1-3 (1).
Table A12.1a Comparison
of Predicted Odour Concentrations at
Countries |
Odour
Concentration |
% Time Compliance |
Averaging Time |
Critical Receptor
Location |
Predicted Highest
3–min Average Odour Concentration at (g) (j) |
Predicted Highest 15-min/1-hour
Average Odour Concentration at (g) (i) (j) |
Remarks |
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TKO Area 137 |
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TKO Area 137 |
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2 (Stringent; Large
population/ close to sensitive receiver) |
99.9% |
3-min |
Residential |
3.86 |
1.90 |
- |
- |
For A1-3 (1), there are 7 no. of exceedance
of odour assessment criterion, which is 0.07% of time over a year which
complies with the 99.9% tile criteria. The predicted 3-min average odour
concentrations at |
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10 |
99.5% |
1 hour |
Residential near piggery |
- |
- |
2.95 |
1.45 |
The predicted 1-hr average odour
concentrations at |
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4 |
99.9% |
3-min |
No. of people >350 but < 2,000 |
3.86 |
1.90 |
- |
- |
The predicted 3-min average odour
concentrations at |
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2 |
99.5% to 99.9% |
1-hour |
High sensitivity of the receiving
environment (worst-case impacts during neutral to stable conditions) |
- |
- |
2.95 |
1.45 |
For A1-3 (1), there are 7 no. of exceedance
of odour assessment criterion, which is 0.07% of time over a year which
complies with the 99.9% tile criteria.
The predicted 1-hour average odour concentrations at |
|
1.5 |
98.0% |
1-hour |
Residential |
- |
- |
2.95 |
1.45 |
For A1-3 (1), there are 7 no. of exceedance
of odour assessment criterion, which is 0.07% of time over a year which complies
with the 98% tile criterion. |
US State of |
1 to 2 |
Highest |
15-min |
Plant Boundary |
- |
- |
2.95 |
1.45 |
For A1-3 (1), there are 3 no. of exceedance
of odour assessment criterion (2 OU), which is 0.034% of time over a year. |
US, |
20 |
<100 hours/ year non-compliance |
- |
Residential with highway |
- |
- |
- |
- |
The predicted highest 5-second average
odour concentrations at TKO Area 137 and |
|
20 |
<100 hours/ year non-compliance |
- |
Rural with growing residential |
- |
- |
- |
- |
The predicted highest 5-second average
odour concentrations at TKO Area 137 and |
Netherland (g) |
3 |
98.0% |
1-hour |
Residential area or other sensitive
receptors |
- |
- |
2.95 |
1.45 |
The predicted 1-hour average odour
concentrations at |
Notes: (a)
EPA 373/07 guideline (Odour assessment using odour source modelling) -
http://www.odournet.com/legislation-.html (b)
http://www.odournet.com/legislation.html (c)
EPA Guidelines on Odour Assessment using Odour Source Modelling,
Updated Apr 2007 (d)
http://www.mfe.govt.nz/publications/air/odour-tr-aug02.pdf (e)
A. P. Van Harreveld; www.env.go.jp/en/air/odor/measure/02_1_3.pdf
(f)
Mahin; http://www.env.go.jp/en/air/odor/measure/02_1_4.pdf (g)
Final Report on Odour Management in (h)
See Annex A12 for detailed
calculations. (i)
The modeling results will be representative for period between 1 hour
to 15-minute averaging time. (j)
The predicted highest 3-min average and 15-min/1-hour average odour
concentrations at TKO Area 137 and |
Annex
A12-2 - Estimation of 3-min and 15min/1-hour Odour Levels for A1-3(1) and A2 |
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(a) |
The
highest 5-sec odour levels were predicted under stability class F at A1-3 (1)
& A2. (Reference to Annex A11-1) |
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(b) |
For
converting 5-sec odour level to 3-minute odour level, a factor of 5 was used
(reference to Warren Spring Laboratory, "Odour Control - A Concise
Guide", 1980) |
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(c) |
For converting
5-second odour level to 15-min/1hour odour level, a factor of 6.9 and 6.55
for stability class D & F, respectively, was used |
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(reference
to RA Duffee, "Odour Modelling - Why and How") |
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A1-3
(1) --- After Rephasing |
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Year |
Month |
Day |
Hour |
Temp |
Wind Speed |
Wind Direction |
Stability Class |
Phase 1 |
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5-sec |
3-min |
15min/1-hr |
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06 |
4 |
8 |
22 |
23 |
0.5 |
128 |
F |
19.3 |
3.86 |
2.95 |
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06 |
3 |
21 |
20 |
0 |
0.7 |
123 |
F |
17.2 |
3.44 |
2.63 |
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06 |
4 |
3 |
20 |
24 |
0.5 |
129 |
F |
16.9 |
3.38 |
2.58 |
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06 |
6 |
26 |
23 |
30 |
0.8 |
128 |
F |
12.1 |
2.42 |
1.85 |
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06 |
1 |
11 |
22 |
19 |
0.6 |
130 |
F |
12.0 |
2.40 |
1.83 |
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06 |
1 |
10 |
19 |
16 |
0.9 |
127 |
F |
11.9 |
2.38 |
1.82 |
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06 |
4 |
7 |
20 |
22 |
1.1 |
126 |
F |
10.5 |
2.10 |
1.60 |
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06 |
3 |
17 |
20 |
0 |
0.8 |
130 |
F |
9.0 |
1.80 |
1.37 |
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06 |
12 |
5 |
18 |
22 |
1 |
129 |
F |
8.5 |
1.69 |
1.29 |
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06 |
6 |
20 |
20 |
29 |
1.1 |
119 |
F |
8.0 |
1.60 |
1.22 |
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06 |
6 |
28 |
18 |
26 |
0.5 |
122 |
D |
7.3 |
1.47 |
1.06 |
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06 |
4 |
25 |
22 |
24 |
1.6 |
122 |
F |
7.2 |
1.45 |
1.11 |
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06 |
12 |
22 |
18 |
19 |
0.9 |
131 |
F |
6.6 |
1.32 |
1.01 |
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06 |
6 |
20 |
19 |
29 |
1.1 |
130 |
F |
6.6 |
1.31 |
1.00 |
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06 |
4 |
3 |
19 |
24 |
1 |
117 |
F |
6.5 |
1.30 |
0.99 |
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06 |
3 |
3 |
19 |
0 |
1.2 |
118 |
F |
6.4 |
1.28 |
0.97 |
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06 |
2 |
23 |
22 |
17 |
1.5 |
119 |
F |
5.9 |
1.17 |
0.90 |
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06 |
6 |
22 |
8 |
30 |
0.6 |
129 |
D |
5.4 |
1.09 |
0.79 |
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06 |
4 |
7 |
19 |
22 |
1.8 |
128 |
F |
5.4 |
1.07 |
0.82 |
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06 |
2 |
8 |
20 |
17 |
0.6 |
133 |
E |
5.4 |
1.07 |
0.82 |
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06 |
4 |
29 |
18 |
25 |
0.7 |
123 |
D |
5.3 |
1.06 |
0.77 |
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A2 ( |
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Year |
Month |
Day |
Hour |
Temp |
Wind Speed |
Wind Direction |
Stability Class |
Phase 1 |
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5-sec |
3-min |
15min/1-hr |
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06 |
1 |
28 |
22 |
16 |
0.7 |
147 |
F |
8.9 |
1.79 |
1.36 |
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06 |
1 |
13 |
19 |
19 |
0.7 |
144 |
F |
8.4 |
1.69 |
1.29 |
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06 |
6 |
21 |
20 |
29 |
0.6 |
150 |
F |
7.9 |
1.58 |
1.21 |
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06 |
6 |
12 |
20 |
26 |
0.8 |
145 |
F |
7.8 |
1.56 |
1.19 |
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06 |
5 |
27 |
22 |
27 |
0.9 |
144 |
F |
6.6 |
1.31 |
1.00 |
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06 |
12 |
22 |
23 |
16 |
0.9 |
149 |
F |
6.0 |
1.20 |
0.92 |
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06 |
3 |
20 |
20 |
0 |
1 |
144 |
F |
5.9 |
1.18 |
0.90 |
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06 |
1 |
16 |
21 |
20 |
0.6 |
152 |
F |
5.5 |
1.09 |
0.83 |
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06 |
12 |
4 |
18 |
21 |
1 |
149 |
F |
5.4 |
1.08 |
0.83 |
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06 |
6 |
2 |
20 |
27 |
1.2 |
147 |
F |
5.2 |
1.04 |
0.80 |
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06 |
6 |
26 |
20 |
30 |
0.5 |
139 |
F |
5.1 |
1.03 |
0.78 |
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Year |
Month |
Day |
Hour |
Temp |
Wind Speed |
Wind Direction |
Stability Class |
Phase 2 |
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5-sec |
3-min |
15min/1-hr |
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06 |
3 |
21 |
20 |
0 |
0.7 |
123 |
F |
9.5 |
1.90 |
1.45 |
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06 |
4 |
8 |
22 |
23 |
0.5 |
128 |
F |
8.2 |
1.65 |
1.26 |
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06 |
4 |
3 |
20 |
24 |
0.5 |
129 |
F |
6.7 |
1.33 |
1.02 |
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06 |
1 |
10 |
19 |
16 |
0.9 |
127 |
F |
5.4 |
1.09 |
0.83 |
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06 |
6 |
26 |
23 |
30 |
0.8 |
128 |
F |
5.2 |
1.03 |
0.79 |
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06 |
4 |
7 |
20 |
22 |
1.1 |
126 |
F |
5.1 |
1.02 |
0.78 |
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