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Consultation as Science Communication: Local Air Quality Management

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empirical reductive-deductive testing of hypothesis ... Sheer range of potential health effects. Complexity of the processes under investigation ... – PowerPoint PPT presentation

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Title: Consultation as Science Communication: Local Air Quality Management


1
Consultation as Science Communication Local Air
Quality Management
PSG 3 18 Oct 2006
Dr Paul Dorfman Faculty of Applied
Sciences University of the West of England,
Bristol, U.K.
2
Whats the problem with quantitative risk
assessment?
  • experimentation, falsification, verification,
    consistency, predictability
  • empirical reductive-deductive testing of
    hypothesis
  • indirect estimation through extrapolation from
    analogous circumstances

3
  • empirical observation supplemented by controlled
    experiments
  • emphasises statistical probabilistic risk
    estimation
  • ensemble analysis and probabilistic
    summariescharacterised by cautious empiricism

4
however, precise determination can be difficult
  • Sheer range of potential health effects
  • Complexity of the processes under investigation
  • Difficulties from information uncertainty
  • Spatial and temporal diffusion of potential
    health effects
  • Dynamic nature and variability of human and
    environmental systems
  • Diagnostic variability of cause-effect
    relationships

5
and there are policy problems
  • Wide range of conflicting value judgements from
    many stakeholders
  • Decision process should be transparent,
    inclusive, build public confidence
  • Modelling and analytic methods which support
    decisions need to deal with inherent complexity
    and uncertainty AND have explanatory power for
    a wide audience

6
the corollary to this is analysis is the
co-construction of risk knowledge
  • broadens the environmental decision-making
    community to incorporate a wider range of
    expertise
  • Reflexive modernity (Beck), citizen science
    (Irwin), civic discovery (Moore)

7
the cultural critique of scientific risk
assessment
  • despite congestion, provides greater
  • democratic legitimacy (accountability,
    transparency)
  • Public take-up
  • Improved efficiency of environmental
    decision-making processes in the long-term

8
backed by EU legislation
  • EU Directive on Public Participation in
    Environmental Plans and Programmes, 2003
  • Public Participation Provisions of the Aarhus
    Convention

9
backed by UK government
  • the more effectively communities are engaged in
    shaping services, the more likely it is that
    quality will be delivered. Indeed, reform and
    modernisation of public services will be not
    accepted as legitimate unless it is based on
    citizens support ODPM/ HO 2005

10
LAQM consultation theory so far
  • Better integration between different policy areas
  • Better understanding of local needs, concerns and
    priorities
  • Local ownership of decisions and proposed
    solutions
  • Improved decisions and better use of resources
  • Active Citizenship

11
initial case study findings
  • LAQM consultation seen as a good thing by LAs
  • LAs perceive that LAQM information provision is
    trusted by communities not a trust problem
  • LAs are trying their best to engage under
    difficult circumstances

12
however
  • LAs are concerned that non-experts have
    difficulties in engaging with complex science
    the public knowledge deficit model
  • LAs struggling to elicit responses from
    consultation exercises response rates can be
    poor

13
One explanation could be..
  • LAs tend to feel more at ease with expert
    statutory consultees than non-statutory
    consultees.
  • Outcomes based on interpretive stances can
    represent effects rather than causes
  • Its possible that consultation mode is informed
    by the value LAs place on differing stakeholders
    LAQM knowledge

14
epistemological chicken
  • LA perception of the relative ability of
    differing stakeholders grasp of AQ science, the
    process that translates that science into policy,
    and their institutional and organisational status
    may transitively determine choice of consultation
    mode - and thus the integration of feedback into
    the LAQM decision-making process

15
another explanation could be timing
  • Does consultation take place at the time and
    point real decisions are made?
  • upstream fundamental science-policy arena
  • Rather than downstream simplified debates that
    are pre-conditioned by upstream decisions

16
meanwhile, LAs have practical concerns about
their current situation
  • The piggy in the middle effect sandwiched
    between central government and local communities.
  • Perceived lack of training and guidance on how to
    improve consultation.
  • Lack of time to effectively carry out
    consultation workload
  • More bureaucracy

17
  • Difficulties in weighting reporting
    community responses and embedding them in the
    decision-making process
  • LAs aware of the relative limits to LAQM can a
    systemic risk be effectively addressed at a local
    level?

18
  • does consultation unfairly lever community
    expectations?
  • does consultation tend to demoralise LA AQM
    public managers?

19
Wider concerns
  • A major concern is how to integrate consultation
    in the decision-making process front-loaded
    or multi-stage process?
  • Real deliberative engagement of a simple
    tick-box exercise?
  • Why engage with consultation if it changes
    nothing? - for both community and LAs

20
our initial inferential analysis suggests
  • current modes of consultation are not working as
    well as they could they do not add sufficient
    value
  • this implies a reasonably comprehensive
    re-conceptualisation of current thinking on the
    form and function of the LAQM consultation
    process
  • This has implications for consultation processes
    in other environmental risk arenas

21
because potentially over-simplified consultation
processes
  • tend to occlude and excise deeper and wider
    contextual concerns held by both LAs and their
    stakeholders who owns a systemic problem?
  • dont address the LAs consultation-implementatio
    n-review problem after consultation, then what?

22
  • doesnt address LAs policy-administration
    problem how can LAs retain legitimacy AND
    flexibility?
  • doesnt address the structure and agency
    problem the role of LAs in the policy-public
    manager-community continuum.

23
core themes
  • How practicable is it to deal with a systemic
    problem at a local level?
  • Has LAQM reached its limits?

24
a change in approach
  • a generalised presumption to lower concentrations
    (in the context of threshold debates) and all
    that implies for the structural embedding of
    joined-up policy making on health protection,
    transport planning, built environment development
    (is health an over-arching determinant?)
  • This has implications for civic engagement that
    is supposed to underpin decision-making processes

25
tentative suggestions for better resolution of
the LA policy-administration dichotomy
  • A reflexive engagement with policy structures
    both top-down and bottom-up models of
    decision-making about shared environmental risks
  • A more holistic approach
  • Public managers (LAs) as civic intermediaries
    (public value theory)
  • Participatory budgeting experiment, e.g. an
    exploratory engagement audit

26
Indicative further work
  • exploring the extent and applicability of
    deliberative processes in other arenas
  • testing the boundaries between the scales (and
    time-scales) of policy intervention
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