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MAKING AN IMPACT?
 SPECIAL CONFERENCE ON STRATEGIC ENVIRONMENTAL ASSESSMENT
               IAIA SEA PRAGUE II 2011
THEME 11 SEA FOR POLICY-MAKING - LESSONS FROM EUROPE AND INTERNATIONALLY
  SESSION 11.2: HOW CAN POLICY SEA CONTRIBUTE TO GREENING GOVERNANCE?



   COOPERATION IN SEA IN A
 DECENTRALIZED GOVERNANCE
          SYSTEM
     Alessandro Bonifazi (Polytechnic University of Bari, Italy)
                                 &
         Carlo Rega (Polytechnic University of Turin, Italy)

                                  21-23 September 2011
22/09/2011
                                  Prague, Czech Republic
 Research Design
    Conceptual Background and Research Questions
    Information about the Context
    Methodology
 Discussion of key issues
    What     is the procedural and substantial nature of institutional
   cooperation in SEA?
      How is institutional cooperation in SEA interfering with the
   environmental governance dynamics embedded in the existing
   planning systems?
      What are the outcomes of institutional cooperation in SEA?


 Conclusions and Future developments

   1/14                    Overview of the presentation
 Strategic     Environmental Assessment (SEA) aims to insinuate
ecological rationalities into systems of governance (Bina, 2007)

 In real SEA processes:
    issues are controversial (on scientific, epistemological and ethical
   grounds);
    social and environmental aspects are intertwined; and
    no single player is empowered with full decision‐making power
   (Bartlett and Kurian, 1999; Nilsson and Dalkmann, 2001; Nitz and
   Brown, 2001; Nooteboom and Teisman, 2003; Runhaar and
   Driessen, 2007)

 Institutional  cooperation and public participation are allegedly
distinctive of SEA when compared to other forms of environmental
assessment



    2/14             Research Design: Conceptual Background
 Is   the implementation of the SEA-Directive in Italy
contributing to fostering institutional cooperation between
planning and environmental authorities?

    What      is the procedural and substantial nature of
   institutional cooperation in SEA?
    How      is institutional cooperation in SEA interfering
   with the environmental governance dynamics embedded
   in the existing planning systems?
    What are the outcomes of institutional cooperation
   in SEA?



   3/14           Research Design: Conceptual Background
Competent
        Authority                  SR= Scoping Report
                                   RO= Reasoned Opinion
       SR         RO               SEA= Strategic
            SEA                    Environmental Assessment
Planning        Environ.           ER= Environmental Report
Authority   ER Authorities




                           Highly
                       decentralised
   ITALY: lagging        planning         (some) REGIONS
       behind
                        system and           forerunners
environmental policy
                        distributed    (planning innovation)
     innovation
                       environmental
                        governance
2/18                   Research Design: Context
 Desktop        analysis of regional SEA systems in
Italy, against the background of evolving national legislation

 30 semi‐structured interviews with key SEA players in
Italy (7 planners, 9 evaluators, and 14 civil servants in local
and environmental authorities), covering also institutional
cooperation

a     dedicated questionnaire survey - only pilot study
completed so far: 15 respondents (similar distribution of
roles as above), 10 regions covered (only 3 with at least
three respondents), 150+ SEA processes considered, mainly
in the spatial planning sector


   5/14                 Research Design: Methodology
 24     different (types of) environmental authorities
reported, but only 6 more prominent (Environment
Protection,         Health,       Protected           Area
Management, Government Departments of Planning and of
Environment, and bordering Local Authorities, plus Water
Catchment Management Authorities in Southern regions)

 Bilateral (technical) meetings and multilateral “ad hoc”
decision bodies, together with trans-organizational informal
interactions are considered the most effective methods to
foster cooperation

Knowledge sharing is clearly the main contribution from
environmental authorities, followed by decision support (on
both SEA and planning processes)

   6/14         Key Issue 1: What Institutional Cooperation?
 As    for the nature and modes of institutional
interactions, it appears to be:

   informative > consultative >> codecisional >>
  implementation-oriented

   cooperative > negotiative >> competitive >>
  conflicting



  7/14       Key Issue 1: What Institutional Cooperation?
*
                   *




Government level where the CA for SEA of municipal spatial plans is established


   8/14             Key Issue 2: Environmental Governance Reloaded
SEA may play a key role under alternative governance arrangements, by altering
the distribution of roles and powers

   PIEDMONT (IT)                   *       CAMPANIA (IT)                  ENGLAND (UK)


 Regional Gov. / Provincial                Regional Government          National Planning
 Gov. / Municipal Gov.                                                  Inspectorate

                                           SEA Reasoned
                    checked                Opinion                                 plan and
  draft plan        plan                                                           ER
                               Provincial
                               Gov.                              Binding report
          Municipality                                           covering all
                                                       ER
                                                                 planning issues
                                                                 including SEA
SEA Reasoned
                    ER
Opinion                       draft plan
                                                                               Local
   Municipal Technical                                                       Authority
                                            Municipality
   Body


     9/14                Key Issue 2: Environmental Governance Reloaded
 Despite    it is a “Reasoned Opinion”, the final SEA
statement includes mainly binding prescriptions concerning
both the SEA process as reflected in the ER and the
plan, but these are very seldom of a strategic nature


 the introduction of SEA arrangements (in the opinion of
respondents):
    had no significant impact on power distribution
   within multilevel governance relationships ,
    resulted in a greater need of coordination among the
   many authorities involved, and
    might raise the status of environmental authorities
   which were not in charge of issuing binding opinions

  10/14        Key Issue 2: Environmental Governance Reloaded
 The most relevant outcomes in terms of pursuing high
policy objectives seem to be:
    increased transparency and accountability
    greater integration of environmental considerations in plan-
   making, whereas
    a poor contribution is made to streamlining procedures and
   reducing time and cost burdens

 Some     environmental policy sectors are being better
integrated in planning through institutional cooperation in
SEA, including:
    SOIL PROTECTION (in terms of hydro-geological risk rather
   than land use and urban sprawl)
    BIODIVERSITY
    LANDSCAPE AND CULTURAL HERITAGE

   11/14            Key Issue 3: Outcomes of Cooperation
 Although all suggested items were deemed relevant, the
most important LIMITING FACTORS             for   INSTITUTIONAL
COOPERATION in SEA seem to be:
    HIGHLY FRAGMENTED environmental governance systems
    LACK       OF    ADEQUATE        RESOURCES   (human    and
   financial), especially for local authorities
    POOR ADAPTATION on the side of environmental authorities
   to the PARADIGM SHIFTS centred on cooperation, both in
   environmental assessment (from control to collaborative
   planning) and in planning (from government to governance)



  12/14              Key Issue 3: Outcomes of Cooperation
 The preliminary results (which will need to be reconsidered once the
study is completed) suggest that no SEA player is able to trigger
significant improvements :

     LOCAL       AUTHORITIES are caught in between DECREASING
       FINANCIAL      ENDOWMENTS       and   increasing    environmental
       responsibilities (Bobbio, 2002; Owen et al., 2007).
       PRACTITIONERS (Planners and Evaluators) operate in SHRINKING
       MARKETS and are bound to loyalty to commissioners (Dahler-
       Larsen, 2006).
       ENVIRONMENTAL AUTHORITIES enjoy very different working
       conditions in terms of the strength of (and public support for)
       their institutional mandates
   Socio-economic dynamics at macro level (e.g. the erosion of local
  authorities’ financial capacity to deliver public policy) affecting
  institutional cooperation and the momentum of SEA at large are
  beyond the scope of our reflections, however…

    13/14             Conclusions and Future Developments
…    to prevent SEA from being perceived as excess administrative
burden, serving purely conservationist goals and trapped into power
games within multilevel governance dynamics, we would argue for:

    better integration into planning systems, irrespective of whatever
governance arrangements is in place
 SEA capacity-building within environmental authorities (training in
planning and evaluation; negotiating the overlaps and interconnections
of tasks and expertise);
 resorting    extensively to ICT-based tools for institutional
cooperation, by tapping into the “Digital Administration Code” agenda
and related funding initiatives
 focusing     scarce resources on truly strategic policies (e.g. the
introduction of environmentally harmful subsidies in the energy sector)
and away from micro interventions currently falling under the scope of
SEA legislation

    14/14              Conclusions and Future Developments
THANK YOU

                            Alessandro Bonifazi
                  Ph.D. in Spatial Planning, MSc in Human Ecology


                Polytechnic University of Bari (Italy),
                Italian Ministry for the Environment
                      email: a.bonifazi@poliba.it

                                   Carlo Rega
             Ph.D. in Spatial Planning, MSc in Environmental Engineering

                Polytechnic University of Turin (Italy)
                     email: carlo.rega@polito.it




22/09/2011

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Bonifazi rega iaia sea prague 2011

  • 1. MAKING AN IMPACT? SPECIAL CONFERENCE ON STRATEGIC ENVIRONMENTAL ASSESSMENT IAIA SEA PRAGUE II 2011 THEME 11 SEA FOR POLICY-MAKING - LESSONS FROM EUROPE AND INTERNATIONALLY SESSION 11.2: HOW CAN POLICY SEA CONTRIBUTE TO GREENING GOVERNANCE? COOPERATION IN SEA IN A DECENTRALIZED GOVERNANCE SYSTEM Alessandro Bonifazi (Polytechnic University of Bari, Italy) & Carlo Rega (Polytechnic University of Turin, Italy) 21-23 September 2011 22/09/2011 Prague, Czech Republic
  • 2.  Research Design  Conceptual Background and Research Questions  Information about the Context  Methodology  Discussion of key issues  What is the procedural and substantial nature of institutional cooperation in SEA?  How is institutional cooperation in SEA interfering with the environmental governance dynamics embedded in the existing planning systems?  What are the outcomes of institutional cooperation in SEA?  Conclusions and Future developments 1/14 Overview of the presentation
  • 3.  Strategic Environmental Assessment (SEA) aims to insinuate ecological rationalities into systems of governance (Bina, 2007)  In real SEA processes:  issues are controversial (on scientific, epistemological and ethical grounds);  social and environmental aspects are intertwined; and  no single player is empowered with full decision‐making power (Bartlett and Kurian, 1999; Nilsson and Dalkmann, 2001; Nitz and Brown, 2001; Nooteboom and Teisman, 2003; Runhaar and Driessen, 2007)  Institutional cooperation and public participation are allegedly distinctive of SEA when compared to other forms of environmental assessment 2/14 Research Design: Conceptual Background
  • 4.  Is the implementation of the SEA-Directive in Italy contributing to fostering institutional cooperation between planning and environmental authorities?  What is the procedural and substantial nature of institutional cooperation in SEA?  How is institutional cooperation in SEA interfering with the environmental governance dynamics embedded in the existing planning systems?  What are the outcomes of institutional cooperation in SEA? 3/14 Research Design: Conceptual Background
  • 5. Competent Authority SR= Scoping Report RO= Reasoned Opinion SR RO SEA= Strategic SEA Environmental Assessment Planning Environ. ER= Environmental Report Authority ER Authorities Highly decentralised ITALY: lagging planning (some) REGIONS behind system and forerunners environmental policy distributed (planning innovation) innovation environmental governance 2/18 Research Design: Context
  • 6.  Desktop analysis of regional SEA systems in Italy, against the background of evolving national legislation  30 semi‐structured interviews with key SEA players in Italy (7 planners, 9 evaluators, and 14 civil servants in local and environmental authorities), covering also institutional cooperation a dedicated questionnaire survey - only pilot study completed so far: 15 respondents (similar distribution of roles as above), 10 regions covered (only 3 with at least three respondents), 150+ SEA processes considered, mainly in the spatial planning sector 5/14 Research Design: Methodology
  • 7.  24 different (types of) environmental authorities reported, but only 6 more prominent (Environment Protection, Health, Protected Area Management, Government Departments of Planning and of Environment, and bordering Local Authorities, plus Water Catchment Management Authorities in Southern regions)  Bilateral (technical) meetings and multilateral “ad hoc” decision bodies, together with trans-organizational informal interactions are considered the most effective methods to foster cooperation Knowledge sharing is clearly the main contribution from environmental authorities, followed by decision support (on both SEA and planning processes) 6/14 Key Issue 1: What Institutional Cooperation?
  • 8.  As for the nature and modes of institutional interactions, it appears to be:  informative > consultative >> codecisional >> implementation-oriented  cooperative > negotiative >> competitive >> conflicting 7/14 Key Issue 1: What Institutional Cooperation?
  • 9. * * Government level where the CA for SEA of municipal spatial plans is established 8/14 Key Issue 2: Environmental Governance Reloaded
  • 10. SEA may play a key role under alternative governance arrangements, by altering the distribution of roles and powers PIEDMONT (IT) * CAMPANIA (IT) ENGLAND (UK) Regional Gov. / Provincial Regional Government National Planning Gov. / Municipal Gov. Inspectorate SEA Reasoned checked Opinion plan and draft plan plan ER Provincial Gov. Binding report Municipality covering all ER planning issues including SEA SEA Reasoned ER Opinion draft plan Local Municipal Technical Authority Municipality Body 9/14 Key Issue 2: Environmental Governance Reloaded
  • 11.  Despite it is a “Reasoned Opinion”, the final SEA statement includes mainly binding prescriptions concerning both the SEA process as reflected in the ER and the plan, but these are very seldom of a strategic nature  the introduction of SEA arrangements (in the opinion of respondents):  had no significant impact on power distribution within multilevel governance relationships ,  resulted in a greater need of coordination among the many authorities involved, and  might raise the status of environmental authorities which were not in charge of issuing binding opinions 10/14 Key Issue 2: Environmental Governance Reloaded
  • 12.  The most relevant outcomes in terms of pursuing high policy objectives seem to be:  increased transparency and accountability  greater integration of environmental considerations in plan- making, whereas  a poor contribution is made to streamlining procedures and reducing time and cost burdens  Some environmental policy sectors are being better integrated in planning through institutional cooperation in SEA, including:  SOIL PROTECTION (in terms of hydro-geological risk rather than land use and urban sprawl)  BIODIVERSITY  LANDSCAPE AND CULTURAL HERITAGE 11/14 Key Issue 3: Outcomes of Cooperation
  • 13.  Although all suggested items were deemed relevant, the most important LIMITING FACTORS for INSTITUTIONAL COOPERATION in SEA seem to be:  HIGHLY FRAGMENTED environmental governance systems  LACK OF ADEQUATE RESOURCES (human and financial), especially for local authorities  POOR ADAPTATION on the side of environmental authorities to the PARADIGM SHIFTS centred on cooperation, both in environmental assessment (from control to collaborative planning) and in planning (from government to governance) 12/14 Key Issue 3: Outcomes of Cooperation
  • 14.  The preliminary results (which will need to be reconsidered once the study is completed) suggest that no SEA player is able to trigger significant improvements :  LOCAL AUTHORITIES are caught in between DECREASING FINANCIAL ENDOWMENTS and increasing environmental responsibilities (Bobbio, 2002; Owen et al., 2007).  PRACTITIONERS (Planners and Evaluators) operate in SHRINKING MARKETS and are bound to loyalty to commissioners (Dahler- Larsen, 2006).  ENVIRONMENTAL AUTHORITIES enjoy very different working conditions in terms of the strength of (and public support for) their institutional mandates  Socio-economic dynamics at macro level (e.g. the erosion of local authorities’ financial capacity to deliver public policy) affecting institutional cooperation and the momentum of SEA at large are beyond the scope of our reflections, however… 13/14 Conclusions and Future Developments
  • 15. … to prevent SEA from being perceived as excess administrative burden, serving purely conservationist goals and trapped into power games within multilevel governance dynamics, we would argue for:  better integration into planning systems, irrespective of whatever governance arrangements is in place  SEA capacity-building within environmental authorities (training in planning and evaluation; negotiating the overlaps and interconnections of tasks and expertise);  resorting extensively to ICT-based tools for institutional cooperation, by tapping into the “Digital Administration Code” agenda and related funding initiatives  focusing scarce resources on truly strategic policies (e.g. the introduction of environmentally harmful subsidies in the energy sector) and away from micro interventions currently falling under the scope of SEA legislation 14/14 Conclusions and Future Developments
  • 16. THANK YOU Alessandro Bonifazi Ph.D. in Spatial Planning, MSc in Human Ecology Polytechnic University of Bari (Italy), Italian Ministry for the Environment email: a.bonifazi@poliba.it Carlo Rega Ph.D. in Spatial Planning, MSc in Environmental Engineering Polytechnic University of Turin (Italy) email: carlo.rega@polito.it 22/09/2011