| Description | Circular 15/1999 |
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| ISBN | n/a |
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| Official Print Publication Date | |
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| Website Publication Date | August 31, 1999 |
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Contents |
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The Environmental Impact Assessment (Scotland)
Regulations 1999
ANNEX A:
INDICATIVE THRESHOLDS AND CRITERIA FOR
IDENTIFICATION OF SCHEDULE 2 DEVELOPMENT REQUIRING
EIA
The criteria and thresholds in this Annex
(referred to in paragraphs 43-44) are only indicative.
In determining whether significant effects are likely,
the location of a development is of crucial importance.
The more environmentally sensitive the location, the
lower the level at which significant effects will be
likely.
It follows, therefore, that the thresholds
below should only be used in conjunction with the more
general guidance in this Circular on "Establishing
whether EIA is required" and, in particular, the
guidance on environmentally sensitive locations (see
paragraphs 36-40)
Agricultural development
A1. In general, agricultural operations fall outside the
scope of the Town and Country Planning system and, where
relevant, will be regulated under other consent procedures.
The descriptions below apply only to projects that are
considered to be 'development' for the purposes of the Town
and Country Planning (Scotland) Act 1997.
Use of uncultivated or semi-natural land for
intensive agricultural purposes
A2. Development (such as greenhouses, farm buildings
etc.) on previously uncultivated land is unlikely to
require EIA unless it covers more than five hectares. In
considering whether particular development is likely to
have significant effects, consideration should be given to
impacts on the surrounding ecology, hydrology and
landscape.
Water management for agriculture, including
irrigation and land drainage works
A3. EIA is more likely to be required if the development
would result in permanent changes to the character of more
than five hectares of land. In assessing the significance
of any likely effects, particular regard should be had to
whether the development would have damaging wider impacts
on hydrology and surrounding ecosystems. It follows that
EIA will not normally be required for routine water
management projects undertaken by farmers.
Intensive livestock installations
A4. The significance or otherwise of the impacts of
intensive livestock installations will often depend upon
the level of odours, increased traffic and the arrangements
for waste handling. EIA is more likely to be required for
intensive livestock installations if they are designed to
house more than 750 sows, 2,000 fattening pigs, 60,000
broilers or 50,000 layers, turkeys or other poultry.
Intensive fish farming
A5. Apart from the physical scale of any development,
the likelihood of significant effects will generally depend
on the extent of any likely wider impacts on the hydrology
and ecology of the surrounding area. Developments designed
to produce more than 100 tonnes (dead weight) of fish per
year will be more likely to require EIA.
Reclamation of land from the sea
A6. In assessing the significance of any development,
regard should be had to the likely wider impacts on natural
coastal processes beyond the site itself, as well as to the
scale of reclamation works themselves. EIA is more likely
to be required where work is proposed on a site which
exceeds 1 hectare.
Extractive industry
Surface and underground mineral
working
A7. The likelihood of significant effects will tend to
depend on the scale and duration of the works, and the
likely consequent impact of noise, dust, discharges to
water and visual intrusion. All new open cast coal mines
and underground mines will generally require EIA. For clay,
sand and gravel workings, quarries and peat extraction
sites, EIA is more likely to be required if they would
cover more than 15 hectares or involve the extraction of
more than 30,000 tonnes of mineral per year.
Extraction of minerals by dredging in fluvial
waters
A8. Particular consideration should be given to noise,
and any wider impacts on the surrounding hydrology and
ecology. EIA is more likely to be required where it is
expected that more than 100,000 tonnes of mineral will be
extracted per year.
Deep drilling
A9. EIA is more likely to be required where the scale of
the drilling operations involves development of a surface
site of more than 5 hectares. Regard should be had to the
likely wider impacts on surrounding hydrology and ecology.
On its own, exploratory deep drilling is unlikely to
require EIA. It would not be appropriate to require EIA for
exploratory activity simply because it might eventually
lead to some form of permanent activity.
Surface industrial installations for the
extraction of coal, petroleum, natural gas, ores, or
bituminous shale
A10. The main considerations are likely to be the scale
of development, emissions to air, discharges to water, the
risk of accident and the arrangements for transporting the
fuel. EIA is more likely to be required if the development
is on a major scale (site of 10 hectares or more) or where
production is expected to be substantial (e.g. more than
100,000 tonnes of petroleum per year).
Energy industry
Power stations
A11. EIA will normally be required for power stations
which require approval from the Secretary of State at the
Department of Trade and Industry (i.e. those with a thermal
output of more than 50 MW). EIA is unlikely to be required
for smaller new conventional power stations. Small stations
using novel forms of generation should be considered
carefully in line with guidance in National Planning Policy
Guideline 6 on Renewable Energy , and Planning Advice Note
45 on Renewable Energy Technologies. The main
considerations are likely to be the level of emissions to
air, arrangements for the transport of fuel and any visual
impact.
Surface storage of fossil fuel and natural gas,
underground storage of combustible gases, storage
facilities for petroleum, petrochemical and chemical
products
A12. In addition to the scale of the development,
significant effects are likely to depend on discharges to
water, emissions to air and risk of accidents. EIA is more
likely to be required where it is proposed to store more
than 100,000 tonnes of fuel. Smaller installations are
likely to require EIA where hazardous chemicals are
stored.
Installations for the processing and storage of
radioactive waste
A.13 EIA will normally be required for new installations
whose primary purpose is to process and store radioactive
waste, and which are located on sites not previously
authorised for such use. In addition to the scale of any
development, significant effects are likely to depend on
the extent of routine discharges of radiation to the
environment. In this context EIA is unlikely to be required
for installations where the processing or storage of
radioactive waste is incidental to the main purpose of the
development (e.g. installations at hospitals or research
facilities).
Installations for hydroelectric energy
production
A14. In addition to the physical scale of the
development, particular regard should be had to the
potential wider impacts on hydrology and ecology. EIA is
more likely to be required for new hydro-electric
developments which have more than five MW of generating
capacity.
Wind farms
A15. The likelihood of significant effects will
generally depend upon the scale of the development, and its
visual impact, as well as potential noise impacts. EIA is
more likely to be required for commercial developments of
five or more turbines, or more than five MW of new
generating capacity.
Industrial and manufacturing
development
A16. New manufacturing or industrial plants of the types
listed in the Regulations, may well require EIA if the
operational development covers a site of more than 10
hectares. Smaller developments are more likely to require
EIA if they are expected to give rise to significant
discharges of waste, emission of pollutants or operational
noise. Among the factors to be taken into account in
assessing the significance of such effects are:
whether the development involves a process designated as
a 'scheduled process' for the purpose of air pollution
control;
whether the process involves discharges to water which
require the consent of the Scottish Environment Protection
Agency;
whether the installation would give rise to the presence
of environmentally significant quantities of potentially
hazardous or polluting substances;
whether the process would give rise to radioactive or
other hazardous waste.
whether the development would fall under Council
Directive 96/82/EC on the control of major accident hazards
involving dangerous substances (COMAH).
However, the need for a consent under other legislation
is not itself a justification for EIA.
Infrastructure developments
Industrial estates
A17. EIA is more likely to be required if the site area
of the new development is more than 20 hectares. In
determining whether significant effects are likely,
particular consideration should be given to the potential
increase in traffic, emissions, and noise.
Urban development projects (including the
construction of shopping centres & car parks,
sports stadiums and multiplex cinemas)
A18. In addition to the physical scale of such
developments, particular consideration should be given to
the potential increase in traffic, emissions, and noise.
EIA is unlikely to be required for the redevelopment of
land unless the new development is on a significantly
greater scale than the previous use, or the types of impact
are of a markedly different nature or there is a high level
of contamination (see paragraph 41).
A19. Development proposed for sites which have not
previously been intensively developed are more likely to
require EIA if
the site area of the scheme is more than 5 hectares;
or
it would provide a total of more than 10,000 m 2 of new
commercial floorspace; or
the development would have significant urbanising
effects in a previously non-urbanised area (e.g. a new
development of more than 1,000 dwellings).
lntermodal transhipment facilities, and
intermodal terminals
A20. In addition to the physical scale of the
development, particular impacts for consideration are
increased traffic, noise, emissions to air and water.
Developments of more than five hectares are more likely to
require EIA.
Motorway service areas
A21. Impacts likely to be significant are traffic,
noise, air quality, ecology and visual impact. EIA is more
likely to be required for new motorway service areas which
are proposed for previously undeveloped sites and if the
proposed development would cover an area of more than five
hectares.
Construction of roads, railways (including
elevated and underground), and tramways
A22. For linear transport schemes, the likelihood of
significant effects will generally depend on the estimated
emissions, traffic, noise and vibration and degree of
visual intrusion and impact on the surrounding ecology. EIA
is more likely to be required for the construction or
improvement of railways and local roads where the new
development is over 2 km in length.
Construction of inland waterways and
canalisation
A23. The likelihood of significant impacts is likely to
depend primarily on the potential wider impacts on the
surrounding hydrology and ecology. EIA is more likely to be
required for the construction or improvement of over 2 km
of canal.
Flood relief works
A24. The impact of flood relief works is especially
dependent upon the nature of the location and the potential
effects on the surrounding ecology and hydrology. Schemes
for which the area of the works would exceed five hectares
or more than 2 km long would normally require EIA.
Construction of airfields
A25. The main impacts to be considered in judging
significance are noise, traffic generation and emissions.
New permanent airfields will normally require EIA, as will
major works (such as new runways or terminals with a site
area of more than 10 hectares) at existing airports.
Smaller scale development at existing airports is unlikely
to require EIA unless it would lead to significant
increases in air or road traffic.
Construction of harbours and port
installations, including fishing harbours
A26. Primary impacts for consideration are those on
hydrology, ecology, noise and increased traffic. EIA is
more likely to be required if the development is on a major
scale (e.g. would cover a site of more than 10 hectares).
Smaller developments may also have significant effects
where they include a quay or pier which would extend beyond
the high water mark or would affect wider coastal
processes.
Dams and other installations designed to hold
water or store it on a long-term basis
A27. In considering such developments, particular regard
should be had to the potential wider impacts to the
hydrology and ecology, as well as to the physical scale of
the development. EIA is likely to be required for any major
new dam (e.g. where the construction site exceeds 20
hectares).
Installation of oil pipelines, gas pipelines
and long-distance aqueducts (including water and
sewerage pipelines)
A28. For underground pipelines, the major impact to be
considered will generally be the disruption to the
surrounding ecosystems during construction, while for
overground pipelines visual impact will be a key
consideration. EIA is more likely to be required for any
pipeline over 5 km long. EIA is unlikely to be required for
pipelines laid underneath a road, or for those installed
entirely by means of tunnelling.
Coastal work to combat erosion and maritime
works capable of altering the coast
A29. The impact of such works will depend largely on the
nature of the particular site and the likely wider impacts
on natural coastal processes outside of the site. EIA will
be more likely where the area of the works would exceed 1
hectare .
Groundwater abstraction and artificial
groundwater recharge schemes; works for the transfer of
water resources between river basins
A30. Impacts likely to be significant are on hydrology
and ecology. Developments of this sort can have significant
affects on environments some kilometres distant. This is
particularly important for wetland and other sites where
the habitat and species are particularly dependent on an
aquatic environment. EIA is likely to be required for
developments where the area of the works exceed 1
hectare.
Tourism and leisure
Ski-runs, ski lifts and cable-cars and
associated developments
A31. EIA is more likely to be required if the
development is over 500 metres in length, or if it requires
a site of more than 5 hectares. In addition to any visual
or ecological impacts, particular regard should also be had
to the potential traffic generation.
Marinas
A32. In assessing whether significant effects are
likely, particular regard should be had to any wider
impacts on natural coastal processes outside the site, as
well as the potential noise and traffic generation. EIA is
more likely to be required for large new marinas, for
example where the proposal is for more than 300 berths
(seawater site) or 100 berths (freshwater site). EIA is
unlikely to be required where the development is located
solely within an existing dock or basin.
Holiday villages and hotel complexes outside
urban areas and associated developments; permanent camp
sites and caravan sites; theme parks
A33. In assessing the significance of tourism
development, visual impacts, ecosystems and traffic
generation will be key considerations. The effects of new
theme parks are more likely to be significant if it is
expected that they will generate more than 250,000 visitors
per year. EIA is likely to be required for major new
tourism and leisure developments which require a site of
more than 10 hectares. In particular, EIA is more likely to
be required for holiday villages or hotel complexes with
more than 300 bed spaces, or for permanent camp sites or
caravan sites with more than 200 pitches.
Golf courses
A34. New 18 hole golf courses are likely to require EIA.
The main impacts are likely to be those on the surrounding
hydrology, ecosystems and landscape, as well as those from
traffic generation. Developments at existing golf courses
are unlikely to require EIA.
Other projects
Permanent racing and test tracks for motorised
vehicles
A35. Particular consideration should be given to the
size, noise impacts, emissions and the potential traffic
generation. EIA is more likely to be required for
developments with a site area of 20 hectares or more.
Installations for the disposal of non-hazardous
waste
A36. The likelihood of significant effects will
generally depend on the scale of the development and the
nature of the potential impact in terms of discharges,
emissions or odour. For installations (including landfill
sites) for the deposit, recovery and/or disposal of
household, industrial and/or commercial wastes (as defined
by the Controlled Waste Regulations 1992) EIA is more
likely to be required where new capacity is created to hold
more than 50,000 tonnes per year, or to hold waste on a
site of 10 hectares or more. Sites taking smaller
quantities of these wastes, sites seeking only to accept
inert wastes (demolition rubble etc.), or Civic Amenity
sites, are unlikely to require EIA.
Sludge-deposition sites (sewage sludge
lagoons)
A37. Similar considerations will apply for sewage sludge
lagoons as for waste disposal installations. EIA is more
likely to be required where the site is intended to hold
more than 5,000 m 3 of sewage sludge.
Storage of scrap iron, including scrap
vehicles
A38. Major impacts are likely to be discharges to soil,
site noise and traffic generation. EIA is more likely to be
required where it is proposed to store scrap on an area of
10 hectares or more.
Waste-water treatment plants
A39. Particular consideration should be given to the
size, treatment process, pollution and nuisance potential,
topography, proximity of dwellings, and the potential
impact of traffic movements. EIA is more likely to be
required if the development would be on a substantial scale
(e.g. site area of more than 10 hectares) or if it would
lead to significant discharges (e.g. capacity exceeding
100,000 population equivalent). EIA should not be required
simply because a plant is on a scale which requires
compliance with the Urban Waste Water Treatment Directive
91/271/EEC.
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