Measuring Environmental Impacts
39. It is not enough merely to ensure that environmental
impacts are simply considered. Where environmental impacts are
assessed in RIAs the accuracy of the assessment remains in question
due to the particular challenge of calculating and presenting
environmental impacts on an equal footing with economic concerns.
40. BRE guidance for officials producing RIAs currently
advises the following approach for presenting impacts:
- "Costs and benefits must
be quantified wherever possible.
- You must show costs and benefits as monetary
values where this is possible. This will allow easier comparison
between the costs and the benefits of each option. The direct
costs of each section must be expressed as monetary values.
[
]
- Record costs and benefits in qualitative terms
only when the above are not possible. Without quantification it
will be less clear what the differences between the options are
and whether the benefits of an option justify the costs."[40]
41. Environmental assessment is often seemingly incompatible
with the convention within RIAs for quantified, and above all
monetised, analysis of impacts. Many environmental issues and
impacts cannot easily be assigned a monetary value. Environmental
impacts are also frequently unpredictable in their extent and
scale, and their true consequences, positive or negative, may
only become apparent over a lengthy period of time. Even the Treasury
Green Book, in its examination of possibilities for evaluating
a number of environmental impacts, acknowledges the complexities
and uncertainties involved in calculating economic values for
environmental damage.[41]
42. In spite of the new emphasis on the economic
cost of climate change in the wake of the Stern Review, we do
not consider monetary totals alone as appropriate for adequately
conveying the extent and coverage of all adverse environmental
impacts. It is difficult to see how an appropriate monetary total
could be arrived at which would adequately communicate the impact
of species loss, or the consequences of climate change on a global
scale, and it is unrealistic to expect officials carrying out
RIAs to be able to achieve this. The BRE guidance for RIAs
suggests a number of methods for analysing difficult-to-quantify
impacts. The particular example provided for environmental benefits
is:
"The environment - you could use surveys
that show people's willingness to pay (how much people would pay
for a clean river, fresh air or a national park) or their willingness
to accept (how much people would be prepared to accept in compensation
for suffering from pollution)." [42]
43. However, Steve Smith of Ofgem made clear to us
the difficulties of such approaches in certain situations, and
why a qualitative assessment can be invaluable:
"Possibly one of the most difficult ones we
deal with is the whole issue of visual amenity with transmission
lines and things like that. That still exercises a lot of thought
within Ofgem, because you can go and do surveys of people who
say to you, 'I'd be willing to pay X not to have a line near my
house', but you are always a bit sceptical unless they are actually
paying it! That is an area where we have had to think about qualitative
as well as quantitative assessment."[43]
44. These methods risk reducing environmental impacts
to a level where the ultimate, wide-reaching consequences are
lost, and a multi-faceted problem is expressed as a one-dimensional
issue. Such trivialisation of environmental impacts can only undermine
attempts to achieve a fair consideration of environmental issues
against economic concerns which are both more adequately assessed
in monetary terms and have greater resonance in this format. Our
predecessor Committee's report of April 2005 expressed these same
concerns, describing how the emphasis on monetisation in RIAs
either leads to environmental impacts being omitted, or to an
inadequate assessment of environmental impacts versus other, more
easily monetised, factors:
"we believe that the emphasis throughout the
RIA guidance [
] on quantifying in monetary terms environmental
impacts is fundamentally mistaken and fails to take account of
the overriding need to meet environmental policy objectives."[44]
45. We continue to support this view. Although some
witnesses to the inquiry, notably Anglian Water,[45]
supported monetisation wherever possible on the grounds thatwithin
the current RIA structure and guidancethis was the only
way to ensure that environmental concerns were considered on an
equal footing with other factors, we believe that the RIA system
as it stands must be reconsidered to ensure that non-monetised
assessment can be successfully included, and that it also must
be recognised as a standard and suitable form of assessment, rather
than an undesirable last resort. We recognise that the field of
quantifying and assessing environmental impacts is an expanding
one, and that considerable effort is being directed into research
towards developing new techniques. We do not, however, consider
blanket monetisation to be a desirable or feasible objective of
impact assessment.
46. The NAO annual evaluation of RIAs for 2005-06
identified at least one RIA from its sample (the RIA for the Department
for Transport's Railways Bill) where "the Department considered
that a sensible quantification of costs and benefits was not possible.
There were, however, no qualitative descriptions where quantification
may have been difficult."[46]
Although this example did not relate to directly environmental
impacts, it does illustrate the dependence on monetised assessment
of impacts and the inability for many RIAs to successfully incorporate
and even accept qualitative analysis. Environmental impacts are
particularly at risk from such behaviour, and it is deeply
unsatisfactory for environmental impacts to be omitted from an
RIA purely because the structure does not easily permit the forms
of assessment which may most suitably convey their importance,
or because there is a reluctance among officials to approach impact
assessment in a non-monetised manner which is seen to contradict
the conventions for RIAs.
47. We recognise that certain areas of environmental
assessment such as greenhouse gas emissions and consequences to
health lend themselves more easily to monetisation. In these instances
it would be both desirable and appropriate to accompany a qualified
form of analysis with a monetised assessment of the impact, in
order to facilitate the comparison of different impacts on these
grounds. We do not, however, believe that monetisation should
ever constitute the sole method of illustrating an environmental
impact, and call for any monetised impact to also be accompanied
by a wider description of the consequences.
48. We continue to support the recommendation
made by our predecessor Committee that, on the RIA summary sheet,
environmental impacts should be broken down and categorised in
non-monetary terms on a plus/minus 7 point scale.[47]
We believe that this will help to break the reliance on monetisation
and will lead to a more effective communication of environmental
impacts. Where possible
and appropriate a quantified or monetised assessment should be
included alongside this rating, and all impacts should be suitably
supported by background analysis and a descriptive assessment
to ensure that the true consequences of the impactbeyond
numbersis understood. Monetisation should not be viewed
as the only suitable form of assessment, or indeed as appropriate
in all situations. Crucially, monetised impacts should not be
viewed by decision makers as somehow more valid or significant
than non-monetised values. We also urge
the BRE to work more closely with academic groups and the private
sector to investigate and consider techniques used successfully
elsewhere for environmental assessment.
49. This difficulty in accurately assessing environmental
impacts also goes some way to accounting for the neglect of environmental
issues in RIAs. Environmental impacts may be identified but then
not included in the RIA due to uncertainty over how accurately
to assess and present them. In their oral evidence, both Ofgem
and Anglian were keen to stress that inadequate analysis and assessment
of environmental issues could well be attributed above all to
the difficult and discouraging nature of such work, rather than
a lack of awareness or a wilful refusal to consider environmental
issues. Steve Smith of Ofgem related the difficulties experienced
in carrying out their impact assessments:
"I do not think people are unwilling but it
is the section they come to and think 'Gosh, this is actually
really difficult', and it does not lend itself as well to the
financial analysis you do in the other sections of the IA. I think
it is all about the commitment you get from whoever is producing
the document to do what would be the hardest part. [
] [I]n
many of the policy issues we deal with it is the most difficult
part to actually work out what the sustainability aspects of the
proposal are."[48]
50. Difficulties encountered when assessing impacts
may also lead to assessments based on incorrect assumptions, the
omission of crucial aspects of a particular impact, or poor presentation
which does not adequately express the impact's significance. The
accuracy of the assumptions behind figures is a particularly crucial
factor in determining the value of an impact assessment. Any value
for an impact assessment will necessarily be based on various
assumptions, assigned values, estimations and predictions. Impact
assessments are unavoidably a "best guess" rather than
indicators of certainty, and current guidance quite rightly encourages
officials to acknowledge this by highlighting any uncertainty,
spelling out assumptions and presenting a range of values where
appropriate.[49]
51. However, it is vital that officials are provided
with the expertise and support to ensure that any assumption acting
as the basis for an impact assessment is as well-informed as possible.
For this to happen officials must have clear and helpful guidance;
the appropriate training and knowledge, in addition to access
to more specialised expertise within the department; a thorough
consultation programme; and a clear process of review, scrutiny
and evaluation.[50]
52. As we have seen, RIAs remain undeniably focused
on cost-benefit analysis. This not only marginalises issues which
do not easily lend themselves to monetisation, but also risks
reducing the full worth of a policy to a narrow balancing of out-of-context
figures. Simon Bullock, Economic Adviser at Friends of the Earth,
expressed particular concern about the need to move from a purely
cost-benefit approach to a more integrated style of assessment:
"one of the difficulties with cost benefit analysis
generally is that it does reduce what should be political complex
decisions to technical bureaucratic ones. [
]. By reducing
everything to one figure, and the costs exceed the benefits, that
hides that complexity."[51]
53. It is precisely for this reason that any monetised
figures need to be supported by qualitative or descriptive analysis,
so that policy-makers can recognise the issues behind the figures.
Similarly, it is essential that any assumptions used as the basis
for figures are also clearly laid out in the document, so that
the figures can be valued appropriately, and effectively challenged
if necessary. BRE guidance currently recommends that policy makers
assess impacts on three levelsa full description, quantification
and monetisation. The NAO's briefing on sustainable development
in RIAs praised the impact assessment for the Electricity and
Gas (Energy Efficiency Obligations) Order 2004, which set out
environmental impacts under all of these categories.[52]
However, it noted that this was the only RIA in its sample of
ten which demonstrated good practice in this respect. [53]
Many RIAs are therefore failing to describe environmental impacts
adequately, leaving certain aspects ambiguous or entirely unexplained.
54. Similarly, although we are in favour of a
short summary sheet for the RIA document as recommended in our
last report,[54]
we are concerned that an increasing reliance on short, monetisation-based
summary sheets might lead to decisions being made without considering
the full conflicts, assumptions and difficulties behind the figures,
or indeed what the impacts actually mean. This is a particular
problem for environmental impacts, which we believe are currently
neglected on the summary sheet due to the emphasis on monetised
figures and trading costs against benefits.
55. We believe that one way to counteract this, and
to reinforce the role of RIAs as a mechanism for implementing
the overarching policy objective of sustainable development, would
be to raise the profile of assessment against sustainable development
on the summary sheet and throughout the document. After all, it
must be remembered that the concept of sustainable development
encompasses far more than simply environmental issues, even though
the term is most often used in that context. As a set of principles
embracing environmental, social and economic development, sustainable
development represents the umbrella concept beneath which truly
integrated policy decisions can be formed, and it must therefore
be placed at the centre of impact assessment.
56. The consultation document produced by the BRE
provides one mention of sustainable development on the summary
sheet, whereby a simple "yes/no" answer is required
for the question "Does the policy comply with sustainable
development principles?"[55]
Although we were encouraged to see a requirement to consider sustainable
development, we were disappointed that it is so superficial. We
believe that an answer of this type fails to acknowledge the different
aspects of sustainable development, provide the Minister signing
off the RIA with any concept of the nuances involved in reaching
this conclusion, or present officials completing RIAs with any
strict criteria for making such a claim.
57. We recommend that the RIA summary sheet should
require a yes/no answer for each of the principles of sustainable
development,[56]
and that a separate section prominent within the main body of
the document (referenced from the summary sheet) covers the assessment
behind each of these responses in more detail. Sustainable development
can only be fully integrated into policy making if it is recognised
as the definitive component for developing and reviewing impact
assessments.[57]
58. We are encouraged by the development of evaluation
tools such as DEFRA's 'Stretching the Web' tool which facilitate
the comparison of different sectors of impact through pictorial
means, shifting the emphasis from trading off monetised figures
in a table to a consideration of the overall worth of the policy
across all sectors. [58]
We would ask the BRE to examine and develop these models with
a view to introducing such tools in the RIA structure in the future.
40 Better Regulation Executive Guidance for RIAs :
Quantification http://www.cabinetoffice.gov.uk/regulation/ria/ria_guidance/costs_and_benefits/quantification.asp
Back
41
The Treasury Green Book, Annex 2, Valuing Environmental
Impactsgives advice on covering many environmental impacts,
and frequently begins each section by commenting on the 'difficulty'
or 'complexity' of placing a value on these impacts - see http://greenbook.treasury.gov.uk/annex02.htm#valuing
Back
42
Better Regulation Executive Guidance for RIAs, Analysing the
Benefits http://www.cabinetoffice.gov.uk/regulation/ria/ria_guidance/costs_and_benefits/analysing_benefits.asp
Back
43
Q 94 Back
44
Environmental Audit Committee, Pre-Budget 2004 and Budget 2005:
Tax, Appraisal and the Environment, paragraph 53. Back
45
See, for example, Ev 10 and Ev 12. Back
46
National Audit Office, Evaluation of Regulatory Impact Assessments
2005-06, HC 1305 of session 2005-2006 Text Box 15, page 19. Back
47
Environmental Audit Committee, Pre-Budget 2004 and Budget 2005:
Tax, Appraisal and the Environment, paragraph 55. Back
48
Q 77 [Mr Smith] Back
49
Better Regulation Executive Guidance for RIAs, Testing your
Assumptions http://www.cabinetoffice.gov.uk/regulation/ria/ria_guidance/costs_and_benefits/testing_assumptions.asp Back
50
These aspects are dealt with in greater detail in Chapters 6 and
7 of this report. Back
51
Q 113 Back
52
NAO briefing document for the Environmental Audit Committee -
'Regulatory Impact Assessments and Sustainable Development', May
2006, Text Box 8, p11. Back
53
Ibid. paragraph 1.25 Back
54
Environmental Audit Committee, Pre-Budget 2004 and Budget 2005:
Tax, Appraisal and the Environment, paragraph 55. Back
55
Better Regulation Executive, The Tools to Deliver Better Regulation
- A Consultation Document, p23. http://www.cabinetoffice.gov.uk/regulation/documents/ria/pdf/consultation.pdf Back
56
The Sustainable Development Strategy sets out five principles
of sustainable development: living within environmental limits;
ensuring a strong, healthy and just society; achieving a sustainable
economy; using sound science responsibly;and promoting good governance.
The Strategy states that for a policy to be sustainable it must
appreciate all five principles. Further detail on the principles
of sustainable development is available at http://www.sustainable-development.gov.uk/what/principles.htm Back
57
Scrutiny and review are discussed in more detail in Chapter 7. Back
58
An example of this DEFRA tool can be seen in Text Box 11 on page
14 of National Audit Office, Regulatory Impact Assessments
and Sustainable Development - Briefing for the Environmental Audit
Committee, May 2006. Back
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