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Odour Threshold Investigation 2012 - Bay of Plenty Regional Council

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In relation to the second question <strong>of</strong> this investigation the groups were spatially different, with<br />

one consisting <strong>of</strong> panellists from Whakatāne and Tauranga (non-geothermal areas) and one<br />

group from Rotorua, where the panellists are frequently exposed to concentrations well<br />

above the international literature odour thresholds. Other basic characteristics <strong>of</strong> the groups<br />

showed that they were generally similar in pr<strong>of</strong>iles when it came to the age and sex <strong>of</strong> the<br />

panellists. The residence time for the Rotorua panellists was also recorded. This was<br />

compared with threshold values for this group. The results showed no relationship with<br />

residence time and average measured threshold.<br />

Several types <strong>of</strong> analysis <strong>of</strong> the grouped data showed that there was a statistically significant<br />

difference between the geometric mean odour threshold results for the two groups (1.1 µg/m 3<br />

for Rotorua and 0.5 µg/m 3 for Whakatāne). The difference was small, but in the direction we<br />

would expect (Rotorua higher than non-geothermal locale). The results also showed that the<br />

human response to odour is highly variable.<br />

The difference between the two groups is interesting in a purely theoretical sense. However,<br />

when taking into account – (i) the wide range <strong>of</strong> thresholds that have been published to date,<br />

(ii) inaccuracies in the methodologies used in these investigations, and (iii) the end use<br />

application <strong>of</strong> thresholds as a comparison point for modelled outputs, the difference shown<br />

between the two groups would be regarded as insignificant and largely treated as being the<br />

same for both. The analysis showed that the vast majority <strong>of</strong> the panellists were able to<br />

detect H 2 S at the 7 µg/m 3 level.<br />

In setting a guideline value it would be dependent on the receiving environments location, as<br />

both groups appear “equal” when it comes to detecting. Variations in odour response would<br />

be dependent on what is commonplace in their local environment. Communities that live in<br />

close proximity to existing or proposed developments or natural settings where H 2 S<br />

emissions are present are equally adept at detecting the odour at low concentrations, when<br />

compared with the Whakatāne group, but more <strong>of</strong>ten than not would be accepting <strong>of</strong> the<br />

odour pr<strong>of</strong>ile because <strong>of</strong> location.<br />

In regard to <strong>Council</strong> air quality policy, the findings <strong>of</strong> this investigation will be used in the<br />

upcoming <strong>Bay</strong> <strong>of</strong> <strong>Plenty</strong> <strong>Regional</strong> Air Plan review process.<br />

ii Environmental Publication <strong>2012</strong>/06–A review <strong>of</strong> odour properties <strong>of</strong> H 2 S <strong>Odour</strong> <strong>Threshold</strong> <strong>Investigation</strong> <strong>2012</strong>

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