% discussion 1000 % - common issues in EIA 400 % - evaluating NZ's approach 600 \section{Discussion} This section discusses common problems of EIA implementations as they relate to the RMA, as well as issues that New Zealand's integrated and devolved approach to environmental assessment brought about. \subsection{The quality of assessments} - poor environmental models / baseline => precautionary principle \textcite{practitioners} - volume of assessment work, enormous breadth in scale of covered projects - those producing an impact assessment are not necessarily skilled in AEE - EIA education is secondary concern for pracitioners (one day courses on AEE) - strong professional ``imprint'' on the AEE process, no common language - no strong central guidance on impact assessment practise --- what is considered adequate is not defined - according to survey of practitioners checklists are most often used, matrices and expert EIA systems are not; checklists are overly simplistic. - Fourth Schedule of the RMA was most often cited as an issues checklist for assessment - assessments are not seen as enabling affected parties to get involved in decision-making --- although this is one of the core principles of EIA - results: AEEs are primarily done to fulfill the requirements of the Fourth Schedule, not concerned with meeting international EIA standards/best practise. % TODO http://www.mfe.govt.nz/publications/rma/review-consent-processing-performance-round-one-jan08/html/page4.html poor quality applications are rarely refused as permitted by section 88(3) of the RMA. Once they have been accepted, inadequancies within the application are addressed through the use of section 92; this approach not only delays the processing of resource consents, but also increases the likelihood of poor quality applications to be granted. \subsection{Participation of the public} Although the use of objective measurements and scientific methodology is considered EIA best practice \parencite{principles}, EIA is neither science nor is it an objective process. % TODO: not science: predictions made on the basis of very limited inputs As environmental impact statements are produced by project proponents with the goal to convince decision-makers of the benefits of the project in question, the report is a subjective statement or even a piece of project advocacy \parencite{TODO}. In recognition of this inherent bias, the EIA process calls for the participation of the general public, in particular the participation of affected individuals or interest groups \parencite{wilkins}. It is therefore rather disappointing that even in recent reviews of international EIA practise, public participation remains on a fairly low level \parencite{eia-state-of-the-art}. According to \textcite{RMIT University \& UNU Online Learning. (n.d). Environmental Impact Assessment Open Educational Resource.} ``there is little opportunity throughout the process of EIA for the public to be involved; where involvement is possible it is often limited due to lack of resources (time and expertise)''. Some of the main barriers to public participation cited by \textcite{eia-state-of-the-art} are: poor knowledge of the public about the process; poor provision of information; failure to influence the decision-making process; poor execution of participation methods; and regulatory constraints. As a review of resource consent processing performance in New Zealand indicates, especially the latter three are significant obstacles to public participation in New Zealand. According to the 2010/11 survey of local authorities the New Zealand Ministry for the Environment carries out every two years, only about 6 per cent of all resource consents were notified in some way, with only 4 per cent being publically notified \parencite{rma-survey}. This means that of 36,154 resource consents that were processed across the country over a period of two years, the public was able to provide input on only 1,414 proposals. - opportunities for public involvement? - limited opportunity for the public to influence decisions \subsection{The problems associated with devolution} What sets apart New Zealand's approach to environmental assessment from those of other countries is the devolved mandate, meaning that most resource consents are processed at the lowest level of governance, by district or city councils. - cannot deal well with cumulative effects, because that's best done on a national/regional level \parencite{eia-state-of-the-art} - most resource consents are processed at the district/city level, not at the regional level - \textcite[p 267]{furuseth}: little experience or resources to scrutinise EIA on the local level \subsection{Monitoring and follow-up work} - insufficient monitoring (68\%) \parencite{rma-survey} - one-off projects that don't improve the knowledge basis or affect the assessment of future projects \parencite{follow-up} \subsection{EIA at the policy level} ``Environmental Assessment in a Changing World'' (EAE_10E.PDF, Sadler) \begin{quote} (page 49) [EA under the RMA] ... is indirectly specified for policy statements and strategic plans which local authorities are required to prepare to guide and implement sustainable resource management. Application at this level is variable and, overall, it is concluded that the unique way that EA is integrated into the Act makes evaluation of the effectiveness of implementation difficult \end{quote} (page 164[pdf], 146[published]) \begin{quote} SEA is intended to be an integral part of policy and plan-setting, rather than being applied to them as a separate procedure. The resulting framework, in turn, establishes a context and parameters for subsidiary EIAs, which are required for all resource use consents and where the presumption is for protection via rigorous limits on discharges etc. However, in practice, implementation of the Act is occurring slowly. Experience to date indicates that local governments still rely on project EIA rather than undertaking policy and pian-level assessments, \end{quote} \subsection{TODO: Effective? Does EIA bring about sustainable development?} \textcite{retrospect}: ``EIA generally continues to bring about only relatively modest adjustments of development proposals.'' also seems to apply for NZ resource consents: - only a little more than half a percent of all resource consents are declined \parencite{rma-survey} \subsection{Scratch} \parencite{beattie}: - cannot be science because it makes predictions based on very limited data - EIAs are always political because they are part of a decision-making process - EIAs are necessary because they add valuable information to public discussions on specific proposals - poor communication - failure to predict important impacts The following is from \textcite{RMIT University \& UNU Online Learning. (n.d). Environmental Impact Assessment Open Educational Resource.}: - screening is political because it depends on the values of those who perform the screening checklist from \textcite{intl-perspective}