Select Committee on Environmental Audit Written Evidence


APPENDIX 7

Memorandum from Dr Neil Summerton, CB

  1.  I am an independent non-executive director of both Three Valleys Water and Folkestone and Dover Water Services, both of which are subsidiaries of Veolia Water UK. In 1991-97 I was Director Water, and then Water and Land, in the Department of the Environment. In 1997-2002 I was Director of the Oxford Centre for the Environment, Ethics and Society at Mansfield College Oxford and Director of the Oxford Centre for Water Research. I was a specialist adviser to the Environmental Audit Committee's inquiry into Water Prices and the Environment in Session 1999-2000.

  2.  I submitted evidence to the Environment, Food and Rural Affairs Committee's inquiry into Water Pricing (First Report, Session 2003-04). Paragraphs 21-31 are relevant to the Environmental Audit Committee's present inquiry and they are annexed.

KEY VARIABLES FOR PRICE LEVELS

  3.  The Committee's announcement of its inquiry refers to the balance that needs to be struck between the size of the environmental programme and price increases to customers, and the proposal. To my mind, this is to put the matter too simply. There is a number of interacting variables which have to be taken into account in deciding the appropriate level of water prices (bearing in mind the important statutory constraint that the regulator must ensure that water companies properly carry out their functions and must ensure that the companies have the necessary revenue to enable them to do so (s. 2 of the Water Industry Act 1991)). The main ones are:

    (a)

    new investment to protect and improve

    (i)

        the quality of drinking water

    (ii)

        the environment (whether from upstream risks of over-abstraction or from downstream risks of pollution)

        This new investment can result from the requirements of European law or of domestic law. The scope for discretion in respect of the former tends to be limited. The extent to which the latter is discretionary depends very much on the structure of the particular legislation, in particular the degree of discretion allowed to the Environment Agency and other regulatory bodies concerned, and to sewerage companies in so far as statutory duties may bear directly upon them.

    (b)

    The cost of maintaining and improving standards of service (these cover a wide range of matters such as meeting growing demand against the background of the effects of climate change, customer care, water pressure, sewer flooding, containing and reducing leakage, and so on). Statutory regulators judge and penalise water companies on these matters.

    (c)

    capital and operational expenditure to maintain networks and plant. System assets are crucial to effective water and sewerage services which are highly capital intensive. These assets have been acquired over two centuries with important spurts at various points in the 20th century. Their lives vary with the nature of the asset and the character and quality of the original provision. They can also vary with the changing environment of the network, eg, with changing ground conditions over time and, where pipes are laid under the highway, with increasing traffic volumes and axle weights. Generally water networks have long lives, but they do not last for ever. Refurbishment and/or replacement is necessary, as with the capital equipment of other industries (which almost always have much shorter replacement cycles than is the case with water). If refurbishment and replacement are not done in a timely way, even with such long-lived assets, the result will be deteriorating standards of service for customers and/or greater operational costs to be borne by customers in order to try to maintain a given standard of service.

    (d)

    The scope for efficiency savings on the part of companies. There is an increasing recognition that the high rate of efficiency savings achieved in the 15 years since privatisation cannot be sustained into the future, though some will still be possible. A once-for-all price cut was possible in 2000 as a result of efficiency savings since 1989, but it is not likely to be repeatable.

    (e)

    The cost of capital, that is, the price that must be paid in the capital markets in competition with other demands for capital, to obtain the capital needed by the companies, whether by way of equity money or loans. Clearly, customers should not be burdened with a higher cost of capital than is necessary to obtain the capital that is needed. Any regulated sector is susceptible to what is seen by investors as "regulatory risk". In this case if the regulator depresses the allowed cost too far in his price determinations, the capital markets may be discouraged from investing in the sector. As Dr Dieter Helm told the Environment, Rood and Rural Affairs Committee last October the cost of capital allowed in 2000 "induced a significant flight-from-equity" (House of Commons Environment, Food and Rural Affairs Committee, Water Pricing, First Report of Session 2003-04, Ev. 83, para. 12).

  4.  At different stages in the Periodic Review, attention tends to shift between these variables. At present, the focus is on the level of new investment for quality purposes, since the government must make what are quite rightly political decisions about the level of new investment which the regulator must take into account in reaching his price determination. But it should not be forgotten that, for any given level of prices, the variables are interactive. The regulator has a statutory duty to enable each company to finance its functions. Statutorily speaking, whether customers can afford the outcome does not come into the matter. Politically and practically, of course, affordability does matter, particularly as the protections hitherto afforded to poorer customers are gradually eroded.

SCALE OF NEW INVESTMENT

  5.  At this stage, the scale of new investment required is critical. It has to be considered in the light of the implications for price levels and for the other key variables. The decisions must bear in mind the possibility that, in the interests of keeping price levels down, the regulator will forced to make unrealistic decisions about efficiency savings and the cost of capital, and forced to cut back, yet again, on the necessary maintenance and replacement of assets. The decision on new quality investment is not easy, of course, precisely because of the extent to which it is statutorily required. This is not a new phenomenon in Periodic Reviews. Nor is this a question of demonising quality investment (see recommendation (b) of the Committee's report of November 2000). It is to recognise that the matter should not be considered in isolation.

MAINTENANCE AND REPLACEMENT OF ASSETS

  6.  The point about maintenance and replacement of assets should be of particular concern to the Committee. In November 2000 the Committee was particularly critical (recommendation (l)) of the way in which the matter was treated in the 2000 Periodic Review and it recommended a collaborative approach between those concerned, to deal with the "intellectual neglect of this important problem". The approach was to be "forward looking and should enable the companies to adequately prepare to renew and repair the cohorts of sewers and mains which will come up for renewal/rehabilitation . . ." The regulators and the companies have worked together closely to implement that recommendation and I believe that it is accepted that, in general, estimates of future requirements are better founded than in the past. It would be a pity if decisions on other matters were again to result in neglect of replacement and to frustrate the benefits of the Committee's earlier recommendations on this topic.

  7.  More generally, the needs of clean water supply should not be crowded out by pressure from the wastewater side.

February 2004

Annex

Extract from evidence to the Environment, Food and Rural Affairs Committee, October 2003

(a)   Reasons for price increases

  21.  The main reason for rising prices in real terms since 1989 has been the cost of investment to raise standards of performance in a number of ways:

    —  Improvements in drinking water quality, in particular investment to deal with nitrates, pesticides, lead and parasites such as cryptosporidium. This investment has been necessary to enable regulatory standards to be met. This has also entailed extra operating costs.

    —  The costs of protecting the environment in two ways:

Dealing with the effects of abstractions, including improving flow in low-flow rivers and protecting and enhancing wetland habitats

—  Reducing environmental impacts of sewage discharge and sludges. Here, a very wide range of regulatory requirements have had to be met, ranging from the bathing waters directive, the freshwater fish and shellfish waters directives, and the urban wastewater treatment directive. These requirements have been exceptionally heavy.

—  Costs of raising quality of service in a variety of ways—nothing equivalent to levels of service requirements existed under the previous nationalised regime.

PROSPECTS FOR THE 2005 REVIEW

  22.  At privatisation, there was a tendency to regard extra investment as a hump that could be surmounted within a decade or so. Thereafter, it was expected, cost pressure would reduce, allowing water prices to fall back to a pattern of RPI—X rather than the RPI + X needed in the first phase. It is already clear however that this happy position will not be achieved in the next review.

(a)   Continuing cost pressures

  23.  There continues to be a wide variety of pressures requiring further new investment, pressures which will also result in new operating costs. Among the more important are:

    —  Achieving the requirements of existing EU directives.

    —  The Water Framework Directive.

    —  Protection of SSSIs and other EU and domestic environmental areas.

    —  Climate change and water scarcity, coupled with rising demand from domestic users.

    —  Leakage control.

    —  Ending sewer flooding.

    —  Eliminating lead from drinking water.

    —  The requirements of the Security and Emergency Measures Directive.

  Beyond this, is the risk of newly-perceived health threats resulting from water re-use. There is also a variety of other variables over which neither the industry nor regulators have any control, such as levels of business rates after the next revaluation, tax and NI changes, the prospect of statutory lane rental charges for works in the highway, abstraction charges, pensions costs, energy costs, general insurance costs, and so on.

(b)   Replacement and renewal

  24.  Additionally, replacement and renewal cannot continue to be neglected. Water companies have to invest in replacing underground networks and above ground plant. At replacement cost, the total value of water assets now exceeds £204 billion. While the life of some categories of this investment is long, it does not and cannot last for ever. That provided in former generations varied in quality through time and geographically. Some old networks need surprisingly little maintenance; others do not last as long or otherwise need replacement in order to provide a good standard of service and reduce maintenance costs. In general, above ground plant needs replacement more frequently than networks.

  25.  Adequate levels of replacement are essential if customers of the future are to receive good service. Assets worth over £200 billion presuppose an annual replacement cost in excess of the current peak rate of £1.7 billion, if an appropriate spread of asset lives is assumed. As noted by the Environmental Audit Committee in 2000, there was a tendency in earlier reviews for OFWAT to neglect this aspect of investment. Since 1999 there have been improvements in the system for identifying these needs. It is important that regulators should recognise the implications for investment levels.

(c)   Implications for prices

  26.  These investment requirements are not well understood by the public. Nor is it appreciated that, while there is no charge for water as a raw material, the costs of networks and treatment plants and operating them are inevitably substantial. Price pressures derive from the extra costs of the service rather than from profits per se, though the costs of capital must be met (as they would have to be met in a publicly-funded service).

  27.  Many of the price pressures are on the wastewater side. What is of particular concern to water suppliers is the possible temptation to achieve environmental improvement at the expense of investment in water supply, and replacement and renewal generally—that the needs of the clean water sector will be crowded out by the wastewater side. The regulator must discharge his statutory duty company by company and he must guard against the possibility of successful appeal to the Competition Commission if he were to allow the needs of the wastewater side to cloud his judgment about those of water suppliers. But it is possible to contain pressures by taking a narrow view of the functions of water suppliers.

FINANCIAL AND EFFICIENCY VARIABLES

  28.  Prices also depend on assumptions about a number of financial and other variables. Here again there are limits to the regulator's room for manoeuvre.

  29.  First, the economic regulator has statutory duties which cannot be ignored and have implications of price levels:

    —  To ensure that water companies carry out their functions; there is little room for manoeuvre to manipulate interpretations of those functions.

    —  To ensure that these functions can be financed, particularly but not exclusively as regards the cost of capital. This is determined by the markets. If efforts are made to squeeze margins below the level that the markets deem acceptable, they will react accordingly. This is in essence what happened following the 1999 price determination.

  30.  Since 1999 there has been extensive revision of the financial structure of companies, increasing levels of debt finance and reducing equity. To some extent, this has been in the longer-term interests of customers, that is, if the level of equity exceeded that necessary for entities with the risk-profile of water companies. However, the result of squeezing returns may have been to cause a reduction of equity beyond the level that is wise. Equity capital in water companies represents a buffer which protects customers from unforeseen or miscalculated risks. If equity has been reduced to below the "right" level, risks will have been increased for customers. These considerations need to be borne very carefully in mind in the present price review, especially in considering the temptation to keep down prices by manipulating financial variables in the face of unavoidable investment pressures.

  31.  A further variable which may be prayed in aid to keep prices down in the face of other pressures is assumptions on the efficiency gains which companies can be expected to make in the next price period. Insofar as private companies can be expected to be more efficient than nationalised companies (or than the former statutory private companies), the period since 1989 ought to have been sufficient to enable the implicit step change to have been completed. Henceforth, it is questionable whether water companies can make greater efficiency gains than private sector companies generally. In this context, two points need to be borne in mind:

    —  The RPI subsumes the underlying rate of efficiency gains across the economy as a whole. If there was no extra investment and prices were restricted to the increase in the RPI, companies would need to achieve at least the average efficiency gain across the economy as a whole. The RPI—X formula therefore requires regulated companies to achieve an additional efficiency gain over and above the underlying average.

    —  As in the case of any company, water companies have costs that they can control and costs (like tax, rates and so on) which they cannot control or even influence. The ratio of controllable to uncontrollable costs is roughly 80:20. Efficiency gains must be concentrated in the area of controllable costs. This means that if the regulator's efficiency assumption is 4% overall, water companies must actually achieve a gain of 5% on controllable costs. This point is of significance if the level of uncontrollable costs is comparatively high compared with the activities which the regulator uses as the benchmark.

  32.  All this emphasises the need for the Committee to be realistic both about the cost pressures on the industry and the extent to which there is freedom nevertheless to hold down prices in the face of these pressures.





 
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