Another Reduction in Emissions

ANAO Report No.11 2014–15 The Award of Grants under the Clean Technology Program 96 indicators under the assessment of merit criterion one, the assessment of the primary merit criterion was inconsistent with the policy proposal for the programs. Specifically, the policy proposal identified that the programs were designed to deliver ‘transitional, targeted assistance for manufacturing companies’ that ‘will assist in achieving the objective of the carbon price by helping these businesses to reduce their energy consumption in the short‐term while remaining competitive in Australia’. The combination of the indicator scores resulted in a score which reflected a mixture of short‐ and long‐term benefits.

4.18 However,

as discussed in paragraph 4.5, indicator two was replaced, in assessing applications against merit criterion one, by grant funds per tonne of carbon abated, which is a relative cost‐effectiveness measure. In other grant programs audited by ANAO where the cost per unit is an important consideration in the award of funding, agencies have included a separate value for moneycost effectiveness merit criterion. 114 This approach provides greater clarity to applicants as to how the merit of their application will be assessed, and promotes a clear line of sight between the program objective and the key policy criterion or criteria.

4.19 The

department used the cost‐effectiveness indicator to assess applications against merit criterion one from the start of the programs, but did not communicate this to applicants until the fifth version of the customer guidelines December 2012. In this version of the customer guidelines, rather than identifying the cost‐effectiveness indicator as the second indicator used in the assessment of applications, the department identified this indicator as a factor that was taken into account. In June 2014, the department advised ANAO that: We took the view early in the program not to reference dollars per tonne in the customer documentation as we felt that this might drive applicants to artificially adjust their projects to achieve a “competitive” dollar per tonne figure. We were also cautious about managing customer messaging around what a competitive figure looked like. This is because there could be significant variation depending on the nature of the emissions reduction measure. However, due to customer feedback on this issue we included a clear 114 See for example ANAO Audit Report No. 25 2013–14, Management of the Building Better Regional Cities Program, and ANAO Audit Report No. 17 2012–13, Design and Implementation of the Energy Efficiency Information Grants Program. ‐ ‐ ‐ ‐ ‐ ‐ ANAO Report No.11 2014–15 The Award of Grants under the Clean Technology Program 97 reference to dollars per tonne in the customer guide published on 12 December 2012 and merit criteria fact sheet published on 16 October 2012.

4.20 In

light of the approach taken to assess applications using different activity boundaries as discussed in paragraph 4.10 IA placed more emphasis on grant funds per tonne of carbon abated when assessing applications against merit criterion one. In this context, the decision not to publish the second indicator used in assessing applications at the start of the programs reduced the transparency of the assessment process, particularly for those applicants who submitted an application prior to December 2012. Implementation of the scoring methodology for merit criterion one

4.21 The

department implemented the scoring methodology for merit criterion one using two rating scales. These rating scales, and the assessment procedures used by the department, evolved over the life of the programs. In this context, ANAO examined the implementation of the scoring methodology in respect to the two indicators used in assessing applications against this criterion, including the rating scales and the relative weightings that resulted from changes made to those rating scales during the life of the programs. Predicted reduction in carbon emissions intensity

4.22 A

maximum of 42 points was available for the predicted percentage reduction in carbon emissions intensity and, as shown in Table 4.2, there were two versions of the rating scale that the department applied to allocate a score for this indicator. The rating scale most frequently used by departmental assessors was the scale that was applied from June 2012 to July 2013. This scale was used to score over 80 per cent of applications.