Overview of costs and benefits associated with regulation in Scottish agriculture
Research providing an overview of the regulations in Scottish agriculture and exploring 12 case studies in further detail.
5. SSI 2000 No. 323 The Pollution Prevention and Control (Scotland) Regulations 2000
Abstract
The Pollution Prevention and Control (Scotland) Regulations 2000 established a new pollution control regime based on the application of Best Available Technology. They apply to what are considered to be the industries posing the greatest risk of pollution, including intensive pig and poultry installations above a certain size threshold. Robust valuation of the costs and benefits of the regulations is beyond the scope of the case study, instead the possibility of using existing Standard Cost Model ( SCM) derived data to assess the admin costs of the PPC regulation in Scotland is explored. The conclusion is that for a regulation such as PPC, which covers a diverse range of industries, the standard cost is likely to lead to significant under or overestimates for some industries. Specifically, it is likely that estimation of the admin costs of the PPC regulations based on unadjusted standard costs from the ABME will lead to significant overestimates for intensive agriculture in Scotland. In order to use the SCM approach, the way in which the standard costs may vary between sectors should be identified and the standard costs adjusted to account for:
- Differences between the agricultural sector being analysed and the overall mix of industries and businesses used to generate the standard cost
- Differences between the same agricultural sectors in Scotland and the rest of the UK
Introduction
SSI 2000 No. 323 The Pollution Prevention and Control (Scotland) Regulations 2000 (hereafter referred to as PPC) transpose EC Directive 96/61/ EC on Integrated Pollution Prevention and Control ( IPPC) into Scottish legislation. The regulations establish a new pollution prevention and control regime for the following sectors: fuel production and combustion; metal production and processing; mineral industries; the chemical industry; waste management installations; pulp and paper manufacturing; textile dyeing; tanning plants; slaughterhouses; food and drink processing plants; animal waste disposal/recycling plants; intensive pig and poultry installations. Only pig and poultry units above the following thresholds are covered by the regulations:
- >40,000 places for poultry
- >2000 places for production pigs (over 30kgs)
- >750 places for sows
Webb et al (2006) reported that approximately 40% of the UK pig herd and 70% of the UK poultry herd are covered by the PPC. There are currently (August 2008) 62 poultry units and 23 pig units above the threshold in Scotland.
PPC seeks to prevent and control pollution "by the application of BAT (Best Available Technology). (European) Guidance on what constitutes BAT is provided by a " BAT" Reference Document (known as a BREF)" Beaton et al (2007, p450). The application procedure for intensive agriculture is no different to any other PPC site as the procedure for processing an application is set down in the Regulations. However SEPA did put together an agriculture specific application form with the intention of reducing (as far as possible within the law) the amount of information required as part of the application and reducing the administrative burden on the industry. The Standard Farming Installation Rules represent SEPA's view of BAT for the sector and have been arrived at after extensive consultation with the industry. If a business expresses an intention to comply with the standards in the rules filling in the application form becomes much easier.
No specific Regulatory Impact Assessment ( RIA) was carried out for the Scottish regulations; however the fourth consultation paper on the IPPC Directive had a Regulatory and Environmental Impact Assessment in Annex 2 ( DETR 1999). The assessment is brief and does not provide any specific analysis of the intensive agriculture sector. The costs and benefits across all industry, as outlined in the assessment, are given in table 1.
Table 1. Costs of and benefits of PPC for ALL industry (from DETR 1999) |
|||
Summary Table of Costs, Benefits and Effects on Charges |
|||
Measure |
Benefit |
Cost |
Effect on Charges? |
---|---|---|---|
Public consultation limited to changes which harm environment plus contentious cases |
Decision time for other changes reduced from 4 months to 3 |
Nil |
No |
Scope for less frequent permit reviews |
More stable planning horizon for industry |
Cost savings |
Scope for reduced subsistence charges |
Standard application forms/permit conditions |
Reduction in regulatee and regulator staff input needed to secure a permit |
Cost savings |
Scope for reduced application charges |
Site condition report on application and surrender |
Removes need to extend financial security to all installations |
£1-200 to £several tens of thousands of pounds per installation |
Need to consider site remediation at application stage will add to charges |
Energy efficiency measures |
3 million tonnes carbon savings. Annual cost savings £650m |
£2 billion capital costs |
Extra factor in environmental appraisal at application stage will add to charges |
Inclusion of remaining 440 IPC installations in IPCC regime |
Reduction in number of regulatory systems |
Site report and energy efficiency costs as above |
Scope for reduction in charges due to lower regulator costs |
Identifying the main costs and benefits of PPC in intensive agriculture
Tables 2 and 3 outline the main costs and benefits arising from the implementation of the PPC regulations in intensive agriculture.
Table 2. The main costs of PPC in intensive agriculture (sources: DETR 1999;https://www.abcalculator.berr.gov.uk/) |
|
Action |
|
---|---|
Admin |
Applying for a permit |
Keeping records and co-operating with inspections |
|
Various minor information obligations |
|
Policy |
Upgrading facilities to prevent or minimise polluting emissions |
Table 3. The main benefits of PPC in intensive agriculture (sources: DETR 1999) |
|
Private |
Dependent on which baseline the benefits are measured relative to: small relative to the situation prior to the implementation of PPC as intensive units did not have to apply for a permit, however, relative to other industries, intensive agriculture has benefitted in terms of reduced labour as a result of standard application forms and conditions. |
---|---|
Decision time reduced |
|
Less confusion |
|
Social |
Prevention of pollution incidents and reduced impact on water environment |
Reduced NH3 emissions |
|
Reduced noise, odour and dust |
Intensive agriculture units were required to apply for a permit by the end of January 2007. SEPA subsequently undertook inspections of these sites and:
"found pollution occurring at 25% of the sites. This pollution was associated with inadequate slurry storage, run-off from contaminated yards, the discharge of wash water from cleaning and disinfection operations, leaking oil storage facilities and feed spillages. Six sites had odour issues and between 20-25% have failed the initial screening for ammonia impact". (Virtue and Morris 2008)
The inspection results show that there is considerable potential for improvements in environmental performance through the PPC regime; prior to the PPC inspections these sites had not been visited by SEPA staff.
Quantifying the main costs and benefits
Robust valuation of the costs and benefits of the PPC regulations would require significant data gathering (e.g. a survey of the PPC-related admin and policy costs in Scottish pig and poultry units; estimation of the reductions in NH3 emissions, noise and odour and water pollution incidents attributable to the regulations; construction of a counterfactual so that the additional costs and benefits of the regulations could be identified etc.). Analysis of this kind is beyond the scope of this short case study. Instead, the case study explores how existing Standard Cost Model data from UK central government sources could be used to estimate the admin costs of the PPC regulations in Scotland, and to highlight any limitations of this approach.
Defra (2006, p43) found PPC in England across all industries to be (in terms of its admin costs):
"the most costly regulation within the Environment reporting unit. Its total estimated cost is £45.9m and two IO/ DRs (Information Obligations/Data Requirements) account for over 95% of the total estimated cost. For both obligations, the quantities are comparatively low (less than 2,000 permits) and the key cost drivers are significant internal and external costs. This is particularly the case for the IO/ DR concerning applying for a permit, where the results indicate the more highly regulated industrial sectors draw significantly on external consultancy services to provide the information required to support the application process."
Admin Costs
The admin costs of PPC across all industries were measured using the SCM during Defra's ABME (see table 4). Descriptions of these Data Requirement IDs ( DRIDs) are given in Annex A.
Table 4. Admin costs of the PPC Regulations 2000 in England applied across all industries
(from: https://www.abcalculator.berr.gov.uk/) (£2006)
DRID |
Admin Burden |
DRID |
Admin Burden |
---|---|---|---|
9230 |
£24,611,808 |
9680 |
£35,230 |
43906 |
£13,703,768 |
9452 |
£26,833 |
40151 |
£401,548 |
9514 |
£24,957 |
9318 |
£43,742 |
9347 |
£18,475 |
9681 |
£43,059 |
40183 |
£7,335 |
40181 |
£39,822 |
9773 |
£4,906 |
The admin costs are dominated by two data requirements, DRID 9230 and DRID 43906. The costs of the activities required for each of these data requirements have been analysed using the SCM, and are summarised in table 5. See Annex B and Annex C for full breakdown of the activities.
Table 5. Annual costs of the most expensive data requirements, applied across all industrial sectors
DRID |
Short description |
Annual Unit Cost (£2006) |
---|---|---|
9230 |
Applying to the regulator for a permit to operate an installation. |
£16,564 |
43906 |
Keeping records, providing information on request, and co-operating with inspections. |
£12,402 |
The standard costs used in the SCM approach are based on surveys of costs over small samples of businesses in each of the industries, and are therefore not statistically robust (see chapter 2 for further discussion of the SCM). Due to the data intensive nature of the SCM approach, it is often not possible to develop standard costs for individual industries. So, while it may be possible to use these standard costs to estimate the admin costs of PPC across all industries in Scotland, the standard cost should be adjusted to take into account differences in the industrial mix.
It should be stressed that the standard costs given in table 5 are based on the average cost for an activity across all industrial sectors, not just agriculture. This approach means that the validity of calculations based on the standard cost depends on how much the administrative actions required to fulfil the regulation in one industry are typical of the average costs over all industries. With a regulation like PPC, which covers a diverse range of industries, the standard cost is likely to lead to significant under or overestimates for some industries. Specifically, it is likely that estimation of the admin costs of the PPC regulations based on unadjusted standard costs from the ABME will lead to significant overestimates for intensive agriculture in Scotland, for the following reasons:
- the PPC regulations include industries with large facilities (such as power stations or chemical plants) where the data requirements (and therefore admin costs) will be much greater than in intensive agriculture - this will lead to significant overestimates of the costs of admin activities such as keeping records;
- the cost of applying for a permit was significantly lower for intensive agriculture in Scotland, due to the development of a sector specific application form.
- No intensive agricultural unit was subject to all the data requirements set out in the SCM analysis of PPC;
- The annual admin charge would not include the cost of applying for a permit. This only needs to be done once.
Conclusions
Using unadjusted SCM data from the analysis of the PPC regulations in the UKABME is likely to significantly overestimate the admin costs for intensive agriculture in Scotland. This raises a fundamental question: how appropriate is a standard cost when applied across different industries, or even sub-sectors within one industry? This is particularly relevant to regulations such as PPC, which apply to a diverse range of industries and businesses. In order to use the SCM approach, the way in which the standard costs may vary between sectors should identified and the standard costs adjusted to account for: (a) differences between the agricultural sector being analysed and the overall mix of industries and businesses used to generate the standard cost: and (b) differences between the same agricultural sectors in Scotland and the rest of the UK
References
Beaton, C. Catto, J. and Kerr, G. (eds) (2007) The Farm Management Handbook 2007/08 Edinburgh: SAC
Defra (2006) Administrative Burdens Measurement Exercise Final Report: July 2006 London: Defra
DETR (1999) Fourth Consultation Paper on the Implementation of the IPPC Directive London: DETR
Virtue, A. and Morris, R. (2008) Report on the findings from initial inspections of intensive agriculture sites subject to regulation by Pollution Prevention and Control in Scotland Stirling: SEPA
Webb, J., Ryan, M., Anthony, S.G., Brewer, A., Laws, J., Aller, M.F. and T.H. Misselbrook (2006) Cost-effective means of reducing ammonia emissions from UK agriculture using the NARSES model Atmospheric Environment 40 7222-7233
Annex A Description of the data requirements for PPC across all industries
(from:https://www.abcalculator.berr.gov.uk/)
DRID |
Admin Burden |
Obligation description |
---|---|---|
9230 |
£24,611,808 |
View | Calc |
43906 |
£13,703,768 |
View | Calc |
40151 |
£401,548 |
View | Calc |
9318 |
£43,742 |
View | Calc |
9681 |
£43,059 |
View | Calc |
40181 |
£39,822 |
View | Calc |
9680 |
£35,230 |
View | Calc |
9452 |
£26,833 |
View | Calc |
9514 |
£24,957 |
View | Calc |
9347 |
£18,475 |
View | Calc |
40183 |
£7,335 |
View | Calc |
9773 |
£4,906 |
View | Calc |
9395 |
£0 |
View | Calc |
9455 |
£0 |
View | Calc |
9503 |
£0 |
View | Calc |
9506 |
£0 |
View | Calc |
9544 |
£0 |
View | Calc |
9697 |
£0 |
View | Calc |
40173 |
£0 |
View | Calc |
Annex BSCM activity breakdown for DRID 9230 (Applying to the regulator for a permit to operate an installation.) Across all industries: (from: https://www.abcalculator.berr.gov.uk/)
Activities calculator screen
Annex CSCM activity breakdown for DRID 43906 (Keeping records, providing information on request, and co-operating with inspections.) For all industries:
(from:https://www.abcalculator.berr.gov.uk/)
Activities calculator screen
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