9c.1.1.1 This section presents the assessment of the potential health risk impacts associated with the operation phase of the IWMF located in both Tsang Tsui Ash Lagoon (TTAL) site and an artificial island near SKC concurrently (i.e. co-exist scenario). A key environmental issue would be the cumulative health impacts during operation phase in the vicinity of the IWMFs at both sites.
9c.2 Prediction and Evaluation of Environmental Impacts
9c.2.1.1 The methodology for the assessment of the potential for compounds of potential concern (COPC) to cause adverse non-carcinogenic health effects is the same as in Sections 9a and 9b.
Classical COPCs of the HKAQO
9c.2.1.2
The highest cumulative annual
average SO2 concentrations predicted at the hot spot areas (as
identified in Sections 3a & 3b) based on territory-wide
scale model results (PATH model) would range from 6 to 17 μg/m3. The average contribution by the IWMF
would range from 0.34 to 3.82%.
Nevertheless, there is still considerable scientific uncertainty as to
whether SO2 is the pollutant responsible for the observed adverse
air effects or, rather a surrogate for particulate matters[1]. While it is not possible to totally rule
out its adverse health effects, the potential additional health effects are
likely to be small.
9c.2.1.3
For the RSP, the highest cumulative annual average
RSP concentrations predicted at the hot spot areas based on territory-wide scale model results (PATH model) would range from 39 to
48 μg/m3. The average
contributions by the IWMF would be below 0.08%. As such, the associated adverse health
effects of RSP due to the IWMF are likely to be very small and are unlikely to
be quantifiable[2].
9c.2.1.4
For NO2, the highest cumulative annual
average NO2 concentrations predicted at the hot spot areas based on territory-wide
scale model results (PATH model) would range from 13 to 40 μg/m3. The average contribution by the IWMF
would range from 0.05 to 1.77%. The
associated additional risk for adverse health effects of NO2 due to the
IWMF are likely to be very small. As
such, it is very unlikely that the NO2 emitted by the IWMF will
cause significant long-term adverse health effects.
9c.2.1.5
The detailed percentage
contributions of SO2, NO2 and RSP by the IWMF are
presented in Appendix 9.3.
Other COPCs
9c.2.1.6 The cumulative non-carcinogenic health impact due to chronic inhalation, includes the impact arising from the IWMF plus the background contribution are presented in Appendix 9.4. Cumulative chronic health impact of the IWMF at all receptors are assessed and compared with the exposure limits/reference levels. It is concluded that the effect are insignificant when compared to the proposed exposure limits/reference levels. No adverse chronic inhalation health effects are expected and no risks due to long-term exposure are expected.
9c.2.1.7 For individual chemicals, hazard quotients have been added across exposure pathways to determine the total non-carcinogenic hazard index (HI) for each receptor potentially exposed to facility-related COPC in the environment. This calculated hazard index (HI) is then compared with the USEPA risk management guidance (USEPA, 1998) suggested initial screening benchmark for exposures of HI = 0.25.
9c.2.1.8 With reference to the risk assessment results on non-carcinogenic hazard presented in Appendix 9.5, it can be concluded that the Hazard Index at all receptors falls under 0.25. The highest hazard quotient occurs at receptor TC4 with a value of 0.02. Therefore, the exposure of the receptors for the co-exist scenario to the non-carcinogenic COPCs is not expected to cause significant adverse health effects.
Cancer Risk
9c.2.1.9 The methodology for calculating potential incremental lifetime cancer risks is the same as in Sections 9a and 9b. The cancer risk from each carcinogenic COPC and from each exposure pathway have been added together to estimate the total cancer risk for each receptor. This calculated total cancer risk is then compared with the target risk level of 1x10-5 stated in the USEPA risk management guidance[3] (USEPA, 1998). In accordance with the USEPA risk management guidance, if a calculated risk falls within the target values, the authority may, without further investigation, conclude that the proposed project does not present an unacceptable risk.
9c.2.1.10 The predicted total carcinogenic risk at the representative receptors are summarized in Appendix 9.5. The calculated risk at all receptors falls within the target risk level of 1x10-5. The highest total cancer risk occurs at receptor TC4 with a value of 3.49 x10-6. Therefore, it is expected that the Project would not present an unacceptable risk.
9c.2.1.11 Since the assessment results meet both the cancer risk and non-carcinogenic hazard index criteria, no further analysis is presumed to be necessary.
Risks due to Short-Term Exposure
9c.2.1.12 In addition to the potential long-term risk to human health presented by COPCs emitted from the facilities, short-term or acute risk has been evaluated for direct inhalation of COPCs. The methodology of determining risk due to short-term exposure is identical to that stated in Sections 9a and 9b.
Classical COPCs of the HKAQO
9c.2.1.13
The average contribution of 1-hr SO2
concentrations by the IWMF are predicted at the hot spot areas identified in Sections 3a & 3b to be in the range
of 0.20% to 10.84%. The highest
cumulative 1-hr average SO2 concentration with the operation of the
IWMF would be 184µg/m3 based on territory-wide scale model results
(PATH model), which is below the short term exposure level with observable
acute health effects in vulnerable groups[4]. Therefore, the associated acute health
effect would be negligible.
9c.2.1.14
For CO, the average contribution of 1-hr CO
concentrations by the IWMF are predicted at the hot spot areas to be less than
0.12%. The predicted highest
cumulative 1-hr average CO concentration is 1712µg/m3 based on
territory-wide scale model results (PATH model) and is far below international
safe levels[5]. Therefore, adverse health effect of CO
contribution from the IWMF is negligible.
9c.2.1.15
For NO2, the predicted highest cumulative
1-hr average NO2 concentration is 275µg/m3 based on
territory-wide scale model results (PATH model). The predicted 1-hr average concentration
is below the level with clear observable acute health effects in many short
term experimental toxicology studies[6]. Nevertheless, the average contribution
of 1-hr average NO2 concentration at the hot spot areas by the IWMF
is predicted to be in the range of 0.04% to 5.38%. Therefore, the acute adverse health
effects of NO2 due to the IWMF would be very small and are unlikely
to be quantifiable.
Other COPCs
9c.2.1.16 The cumulative non-carcinogenic health impact due to direct inhalation includes the impact arising from the IWMF plus the background contributions are presented in Appendix 9.6. Cumulative acute health impact of the IWMF at all receptors are assessed and compared with the exposure limits/reference levels. It is concluded that the effects are insignificant when compared to the proposed exposure limits/reference levels. No adverse acute effects are expected.
Maximum Permitted Concentration of Certain
Metals present in Foods
9c.2.1.17 Based on the assessment results presented in Appendix 9.7, it can be concluded that food grown in the vicinity of all receptor locations would comply with the maximum permitted concentrations stipulated by the Centre for Food Safety. The concentrations of Antimony, Arsenic, Cadmium, Chromium, Lead and Mercury at all receptor locations fall under the maximum permitted concentrations listed in the first and second schedules in Tables 9a.3, 9a.4, 9b.3 and 9b.4.
9c.3.1.1
The cancer risk arising from exposure to compounds
of potential concern (COPCs) associated with the emissions of the IWMF is evaluated in this section. The highest
cancer risk arising from the IWMF (co-exist scenario) is predicted to be 3.49 x10-6 and it is considered that the Project would
not present an unacceptable risk and no further analysis is necessary. The highest predicted total Hazard Index
(HI) at all receptors are well below 0.25, which is derived from a conservative
approach. Cumulative acute
non-carcinogenic health impact of the IWMF imposed to the worst impacted human
receptors were assessed and compared with local and overseas guideline
levels. It was concluded that the
levels of non-carcinogenic chemicals were found to be insignificant when
compared to the adopted/derived reference levels. For the classical COPCs of the HKAQO,
while it is not possible to rule out adverse health effects from the IWMF with complete certainty, the impact on health
from small additional air pollutants is likely to be very small and unlikely to
be quantifiable.
9c.3.1.2
A compliance check of the maximum permitted
concentration of certain metals present in foods due to the Project as
stipulated in “Food Adulteration (Metallic Contamination) Regulations” by the
Centre for Food Safety, was conducted.
The concentrations of Antimony, Arsenic, Cadmium, Chromium, Lead and
Mercury at all receptors fall under the maximum permitted concentrations listed
in the first and second schedules of the Regulations.
[1] WHO Air quality guidelines for particulate
matter, ozone, nitrogen dioxide and sulfur dioxide, Global update 2005, Summary
of risk assessment, World Health Organization
[2] Fourth External Review Draft of Air Quality
Criteria for Particulate Matter (June, 2003), Appendix 9A, USEPA
[3] Region 6 Risk
Management Addendum - Draft Human Health Risk Assessment Protocol for hazardous
Waste Combustion Facilities.
[4] Toxicological Profile for
[5] Toxicological Profile for
[6] WHO Air quality guidelines for particulate
matter, ozone, nitrogen dioxide and sulfur dioxide, Global update 2005, Summary
of risk assessment, World Health Organization