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Ambient Air Quality NEPM

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Environmental impact of not making the measure. Statement of alternative methods ... Direction by a Project Team of regulators from States and Commonwealth ... – PowerPoint PPT presentation

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Title: Ambient Air Quality NEPM


1
Ambient Air Quality NEPM
  • By
  • Dr Tom Beer
  • CSIRO Atmospheric Research
  • CSIRO Environmental Risk Network

2
National Environment Protection Council
  • Set up under IGAE
  • Council of Governments
  • Implement National Environmental Protection
    Measures(NEPM)

(www.ephc.gov.au)
3
National Environment Protection Measures
  • Desired environmental outcome
  • Reason for the proposed measure
  • Environmental impact of not making the measure
  • Statement of alternative methods
  • Economic and social impact
  • Address regional environmental differences
  • Timetable

4
Ambient Air Quality NEPM
  • Started in mid-1996
  • Direction by a Project Team of regulators from
    States and Commonwealth
  • Desired outcomeProtect human health well-being
  • Deal with six criteria pollutants
  • nitrogen dioxide
  • sulfur dioxide
  • carbon monoxide
  • ozone
  • particulate matter
  • lead

5
NEPM - 1998
6
Ambient Air Quality NEPM
7
Exposure Assessment
  • Number of people
  • Air concentration
  • Duration of exposure
  • Used monitoring data plus ABS statistics
  • Metric - Population exposed(person-events)
  • Extreme value metricPopulation affected(persons)

8
Exposure Assessment
P exp(-kc) and exp (-kc-b)
9
Exposure - a complex problem.
  • Objective - a first approximation
  • Problem simplified to OUTDOOR, AMBIENT
    AIR Population stays still (residential
    census) Current pollution levels (1993 - 1995)

10
Exposure assessment methodology
  • Define regional boundary (around populated area)
  • Spatial interpolation of pollution data
  • Map population data onto a 1km x 1km grid
  • Combine pollution population
  • Assess exposure to varying levels of pollution
  • Compute total exposure.

11
Air Pollution
Population
Exposure
12
ExposureModelResults
of person-events/year ( 24-hr average
visibility lt 30 km )
13
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14
Alternative exposure metrics(extreme value
metric)
  • Population affected computed fromANNUAL
    MAXIMUM CONCENTRATIONS,POPULATION DENSITY
  • Gives an independent measure of exposure.

15
(No Transcript)
16
Exposure assessment - results
17
Exposure assessment - results
18
Health Risk Assessment
  • Risk, during a given time, of the scenarios
    under consideration is the union of a set of
    consequences and their associated probabilities
    (Beer Ziolkowski, 1995)
  • Time - 1993 to 1995
  • Scenarios - air quality measurements
  • Consequences - health end-points
  • Probabilities - calculated using exposure and
    dose-response information

19
Health Risk Assessment
  • University of Wollongong/CSIRO
  • Population-based, non-cancer assessment
  • Health end-points for 6 criteria pollutants
  • Exposure assessment (average value of k)plus
    dose-response
  • Dose-response approximated by concentration-respon
    se, based on proportion of people displaying
    symptoms
  • Total number of symptomatic people
  • Normalise by dividing by total population

20
Quantitative Health Risk Assessment
Peak Concentration NOEL 1/k
21
Health Risk Calculations
22
Notional NEPM - Air QualityJuly 1997
23
Standards - Issues
  • Numerical valuePrecautionary Principle
    approach NOEL/(Safety Factor)Risk based
    approach Undetermined
  • Averaging timeStatistical equivalence
  • Allowed exceedances

24
Statistical equivalence
25
CSIRO Concerns
  • Nitrogen Dioxide1 year standard protects
    vegetation
  • Ozone4 hour standard set on medical experiments
    over 6-8 hours
  • Sulfur Dioxide1-day standard 0.15ppm
    statistically equiv.
  • Lead - Air is only one of many pathways

26
Notional NEPM - July 1997
  • Desired environmental outcome
  • Protection of human health well-being
  • Definitions
  • Goal
  • Standard
  • Protocol

27
Draft NEPM - December 1997
28
Future Research Needs
  • ABS Census data is static - people move
  • Australians indoors 95 of the time
  • Fixed monitoring station data - only a first
    approximation
  • NOEL contentious
  • Concentration-response curves
  • Dose-response, individual variability
  • Exposure and health - same dose measure

29
Indoor/Outdoor relationships
  • Effective concentrationWeighted sum of indoor
    and outdoor0.95 Indoor 0.05 Outdoor
  • Effective concentrationas a ratio of
    outdoor0.95 (Indoor/Outdoor) 0.05

30
Indoor/Outdoor relationships
31
Future Air Quality NEPM
  • Stakeholder agreement
  • Collaborative, interactive consultancies
  • Transparent basis for the use of science
  • Adequate time-lines

32
Discussion of issues
  • The NEPM process
  • Setting standards
  • The results of the 1998 NEPM
  • Data requirements
  • Exposure assessment
  • Health risk assessment

33
Issues The NEPM Process
  • Stakeholder agreement
  • Collaborative, interactive consultancies
  • Transparent basis for the use of science
  • Adequate time-lines

34
IssuesSetting standards
  • Numerical valuePrecautionary Principle
    approach NOEL/(Safety Factor)Risk based
    approach Undetermined
  • Choice of averaging time
  • Allowed exceedances

35
IssuesData requirements(NEPM Monitoring
Protocol)
  • Previous lack of national standards in data
    storage and data quality control
  • Need nationally consistent databases and
    software.
  • Need improved spatial coverage
  • Need travel/trip data, indoor/outdoor data.

36
Issues - Exposure assessment
  • Validate estimates using different methods
  • Modelling can be used as a sophisticated
    interpolation method to estimate time variations
    in concentration
  • Implement roadside, indoor and in-vehicle
    models.

37
IssuesHealth risk assessment
  • No agreed health end-points
  • Uncertainty in LOEL values
  • No agreed acceptable level of risk, or method to
    obtain it.
  • Shape of concentration-response

38
Future Research Needs
  • ABS Census data is static - people move
  • Australians indoors 95 of the time
  • Fixed monitoring station data - only a first
    approximation
  • Dose-response, individual variability
  • Exposure and health - same dose measure

39
NEPM Ambient Air Quality NEPC actions
  • Establish A Peer Review Committee.
  • Risk assessment taskforce to report within 3
    years.
  • Reviews ofparticle standard start by 2001SO2
    and O3 - start by 2003NEPM in 2005.
  • Monitor PM2.5

40
NEPM Ambient Air Quality PM2.5
Issues Paper (The need for a PM2.5
Standard) Discussion Paper (Setting a PM2.5
Standard) Technical paper on exposure and risk
characterisation Technical paper on
monitoring Impact Statement for draft
variation NEPM variation (www.ephc.gov.au)
41
NEPM Ambient Air Quality PM2.5 Standard
July 2003 Monitoring to start in 2004 Fine
particle NEPM in force 2005
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