Method Statement - Planning applications search - South Wiltshire
Method Statement - Planning applications search - South Wiltshire
Method Statement - Planning applications search - South Wiltshire
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VINE COTTAGE, FORE STREET,<br />
WYLYE<br />
CONSTRUCTION METHOD<br />
STATEMENT (TO DEMONSTRATE<br />
SAFEGUARDS AGAINST<br />
POLLUTION)<br />
PFA Consulting<br />
Stratton Park House<br />
Wanborough Road<br />
Swindon<br />
SN3 4HG<br />
Telephone: 01793 828000<br />
Facsimile: 01793 835500<br />
E-mail: admin@pfaplc.com
VINE COTTAGE, FORE STREET, WYLYE<br />
CONSTRUCTION METHOD STATEMENT (TO DEMONSTRATE SAFEGUARDS AGAINST POLLUTION)<br />
DOCUMENT CONTROL<br />
Job No. C582<br />
Name Date Initials<br />
Prepared by G EVES 09.02.2010<br />
Checked by G EVES 09.02.2010<br />
Issue Date Comments Approved<br />
1 09.02.2010 -<br />
This document has been prepared for the exclusive use of the client in connection with the project and unless otherwise agreed in<br />
writing by PFA Consulting, no other party may copy, reproduce, make use of or rely upon the contents of this report other than for<br />
the purposes for which it was originally prepared and provided.<br />
Opinions and information provided in this document have been provided using due care and diligence. It should be noted and is<br />
expressly stated that no independent verification of any information supplied to PFA Consulting has been made.<br />
Warning: This document may contain coloured images which may not print satisfactorily in black and white. It may also contain<br />
images originally created at a size greater than A4 which may not print satisfactorily on small printers. If copying is authorised but<br />
difficulty is incurred in reproducing a paper copy of this document, or a scaled copy is required, please contact PFA Consulting.<br />
Authorisation for reproducing plans based upon Ordnance Survey information cannot be given.<br />
FEBRUARY, 2010<br />
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VINE COTTAGE, FORE STREET, WYLYE<br />
CONSTRUCTION METHOD STATEMENT (TO DEMONSTRATE SAFEGUARDS AGAINST POLLUTION)<br />
CONTENTS<br />
PAGE NO.<br />
1. INTRODUCTION...........................................................................................................1<br />
2. METHODOLOGY...........................................................................................................2<br />
3. MITIGATION OF CONSTRUCTION EFFECTS.................................................................4<br />
APPENDICES<br />
APPENDIX 1 SITE LOCATION PLAN<br />
APPENDIX 2 POLLUTION PREVENTION GUIDANCE<br />
FEBRUARY, 2010<br />
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VINE COTTAGE, FORE STREET, WYLYE<br />
CONSTRUCTION METHOD STATEMENT (TO DEMONSTRATE SAFEGUARDS AGAINST POLLUTION)<br />
1. INTRODUCTION<br />
Page 1 of 6<br />
1.1. This statement has been prepared by PFA Consulting on behalf of Mr Mather in<br />
support of a planning application for 3 dwellings within the curtilage of Vine<br />
Cottage, Wylye. The proposal includes the demolition of existing structures on<br />
the site and the infilling of a swimming pool. The purpose of this statement is to<br />
provide assurance that water resources will not be put at risk as a consequence<br />
of the construction works – it should therefore be noted that this is not a<br />
Construction <strong>Method</strong> <strong>Statement</strong> for CDM Regulation purposes or other Health<br />
and Safety issues more generally relating to the works.<br />
1.2. The site is located on the southern side of Fore Street in Wylye some 250m<br />
south of the River Wylye river system. A plan showing the location of the site is<br />
contained in Appendix 1.<br />
1.3. The site is identified by the Environment Agency as lying within a “Zone 1”<br />
groundwater protection zone where activities may represent a special risk to<br />
potable water supplies.<br />
FEBRUARY, 2010<br />
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VINE COTTAGE, FORE STREET, WYLYE<br />
CONSTRUCTION METHOD STATEMENT (TO DEMONSTRATE SAFEGUARDS AGAINST POLLUTION)<br />
2. METHODOLOGY<br />
Page 2 of 6<br />
2.1. This <strong>Method</strong> <strong>Statement</strong> covers the effect of the proposed development on<br />
groundwater and nearby watercourses.<br />
2.2. The site is presently a domestic curtilage forming part of Vine Cottage.<br />
2.3. The nearest watercourse (part of the River Wylye System) is some 250m to the<br />
north. The site does not lie within the identified flood plain of this river system.<br />
2.4. The underlying stratum is upper chalk, which is a major aquifer and the<br />
Environment Agency’s groundwater vulnerability mapping indicates that the site<br />
lies at the edge of a “Zone 1” Source Protection Zone and thus may be<br />
particularly susceptible to pollution as a consequence of poor working practices<br />
on the site.<br />
2.5. It should be noted that the Environment Agency’s records indicate a pollution<br />
occurrence nearby in 2008. It is understood that this was the result of a domestic<br />
oil tank leakage and full remediation has now taken place and accordingly has<br />
no impact upon the methodology or recommendations set out in this statement.<br />
Potential Impacts During Demolition and Construction<br />
2.6. Potential construction impacts on surface and groundwater include fuel spills<br />
and spillage of other potentially polluting materials used for construction. Dust<br />
and the spreading of mud on roads by construction vehicles is also a potential<br />
source of pollution which may also affect the operation of any soakaways on the<br />
site serve existing roads and may pollute groundwater.<br />
2.7. Excavation works may create additional paths into the underlying ground which<br />
may allow polluting material to enter the groundwater regime.<br />
2.8. The process of demolition has the potential to release any pollutant fluids which<br />
may be stored within the buildings to be demolished to the ground and, in<br />
particular, the removal of any fuel tanks or heating systems which may contain<br />
FEBRUARY, 2010<br />
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VINE COTTAGE, FORE STREET, WYLYE<br />
CONSTRUCTION METHOD STATEMENT (TO DEMONSTRATE SAFEGUARDS AGAINST POLLUTION)<br />
Page 3 of 6<br />
heating fuel or the removal of any historic (or existing) sewerage system has the<br />
potential to create pollution.<br />
2.9. There are no surface water sewers which discharge to the river system and there<br />
is no watercourse, or pathway, which would allow pollution to flow directly to<br />
the river system. There is therefore little potential pollution risk to discharges to<br />
surface waters, although pollution to groundwater, which may impact on both<br />
groundwater supplies and on watercourses, will require special consideration<br />
given the sensitivity of the area.<br />
2.10. During construction there is also the potential for surface water to run off the site<br />
and result in flooding of adjacent land, carrying pollutants from the site with it.<br />
2.11. There will be a requirement to accommodate the discharge of foul water from<br />
any temporary site accommodation during the construction phase which has the<br />
potential to cause pollution.<br />
FEBRUARY, 2010<br />
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VINE COTTAGE, FORE STREET, WYLYE<br />
CONSTRUCTION METHOD STATEMENT (TO DEMONSTRATE SAFEGUARDS AGAINST POLLUTION)<br />
3. MITIGATION OF CONSTRUCTION EFFECTS<br />
Page 4 of 6<br />
3.1. A fundamental element of all mitigation measures in respect of construction<br />
effects will be both a proper level of supervision of the works, and effective<br />
contingency plans to deal with accidents and/or unforeseen circumstances.<br />
3.2. The principal contractor for the construction works will have overall<br />
responsibility for the supervision of works, and, under the Construction (Design<br />
and Management) Regulations 2007, is required to be competent and to ensure<br />
that all staff are competent.<br />
3.3. Such competency, combined with the specific measures identified below, will<br />
assist in minimising the risk of pollution during construction.<br />
3.4. Prior to any demolition taking place, any potential polluting liquids shall be<br />
drained to sealed containers and removed from the site to an appropriate place<br />
of disposal. In particular, the possibility of encountering central heating fuel and<br />
swimming pool chemicals are particularly identified. In addition, the possibility<br />
of uncovering an unidentified septic tank, cesspit or other foul drainage system<br />
within the curtilage of the property is identified. Any waste matter which is<br />
found within such structures shall be removed by an authorised contractor.<br />
3.5. During construction, temporary measures will be installed to ensure that no<br />
surface water runs off from the site, or gives rise to risk of pollution to<br />
groundwater or the aquifer from pollutants which may be present on the ground.<br />
Such measures may include temporary settlement ponds and cut off bunds.<br />
3.6. It will be necessary for the contractors to adopt the principles set out in the<br />
Environment Agency’s Pollution Prevention Guidelines Nos. 1 (General Guide<br />
to the Prevention of Pollution); 2 (Above Ground Oil Storage Tanks); 5 (Works<br />
and Maintenance in or near water); and 6 (Working at Construction and<br />
Demolition Sites). The principles set out in these documents include the<br />
measures to be adopted if fuel for vehicles and plant is to be stored on site and<br />
FEBRUARY, 2010<br />
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VINE COTTAGE, FORE STREET, WYLYE<br />
CONSTRUCTION METHOD STATEMENT (TO DEMONSTRATE SAFEGUARDS AGAINST POLLUTION)<br />
Page 5 of 6<br />
refuelling facilities provided. Such measures will ensure that the risk of polluting<br />
material being carried into the groundwater or aquifer will be minimised.<br />
(Appendix 2)<br />
3.7. It may also be necessary for the contractor to provide street cleaning facilities to<br />
keep adjacent roads clear of mud, or other material, which may find its way onto<br />
the adjacent highway, and consequently then being carried into the groundwater<br />
or aquifer.<br />
3.8. In order to minimise the creation of additional pathways for surface water into<br />
the aquifer, close supervision of any excavation works should take place.<br />
3.9. Adherence to general Health and Safety legislation will ensure that all site<br />
personnel are adequately trained, that all plant and vehicles are maintained, and<br />
that adequate facilities are available on site so that the risk of accidents, or poor<br />
working practices, which may result in polluting material being deposited on the<br />
ground and thus giving rise to adverse impacts, is minimised.<br />
3.10. Construction control measures shall include contingency plans to deal with<br />
accidents and unforeseen circumstances. These measures will be continually<br />
reviewed and updated as necessary and, where necessary, will be approved by<br />
the Environmental Health Officer. Such plans will include notices with<br />
emergency contact numbers and the provision of basic spillage protection<br />
equipment.<br />
3.11. The Control of Pollution Act, and the penalties of non-compliance with the<br />
requirements of the Act, together with a commitment to the principles of ISO<br />
14001 will maximise the probability of appropriate measures, including those<br />
identified above, being implemented, and minimise the possibility of<br />
appropriate measures not being adopted. Compliance with the appropriate<br />
measures will provide a high degree of protection and minimise the potential for<br />
pollution of groundwater and any consequential impacts.<br />
3.12. Health and Safety requirements, and good site management, will require<br />
appropriate temporary mess and toilet facilities to be provided on site, and<br />
either temporary connections will be made to the existing public foul sewer<br />
FEBRUARY, 2010<br />
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VINE COTTAGE, FORE STREET, WYLYE<br />
CONSTRUCTION METHOD STATEMENT (TO DEMONSTRATE SAFEGUARDS AGAINST POLLUTION)<br />
Page 6 of 6<br />
adjacent to the site, or sealed, self contained units will be provided with a<br />
regular emptying schedule. This will ensure that any effects from foul water<br />
during construction will not be significant.<br />
3.13. Provided the above measures are put into practice, the risk of pollution during<br />
construction is considered to be negligible.<br />
FEBRUARY, 2010<br />
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Appendix 1
Appendix 2
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UPDATE TO PPG 2<br />
Oil Storage Regulations for Scotland, the Water Environment (Oil Storage) (Scotland)<br />
Regulations 2006 1 , were introduced on 1 st April 2006. PPG2 Above ground oil storage is being<br />
updated to reflect the requirements of these Regulations. A revised PPG2 should be available<br />
by the end of November.<br />
Copies of the Water Environment (Oil Storage) (Scotland) Regulations 2006 can be<br />
downloaded at: http://www.opsi.gov.uk/legislation/scotland/ssi2006/20060133.htm<br />
For sites in England, the good practice guidance and references to the Control of Pollution (Oil<br />
Storage) (England) Regulations 2001, known as Oil Storage Regulations England, in PPG2 are<br />
still up to date.<br />
For sites in Scotland, you should check the specific requirements of the Scottish Regulations<br />
and how they apply to your oil storage. Visit SEPA s website at<br />
www.sepa.org.uk/regulation/oilstorage2006/index.htm or contact your local SEPA office.<br />
The following is a summary of the key requirements of the Scottish Regulations.<br />
Type of Oils<br />
The Regulations apply to any kind of oil including petrol, diesel, mineral oil, heating oil,<br />
lubricating oil, waste oil, vegetable and plant oil but does not include uncut bitumen as it was<br />
considered this material would solidify in the vicinity of any spillage. The storage of agricultural<br />
fuel oil in Scotland is now controlled by these Regulations.<br />
When do the regulations come into effect?<br />
The regulations come into force in 3 stages:<br />
1. New tanks installed after 1 April 2006 will have to comply by 1 October 2006.<br />
2. Existing tanks within 10 metres of surface water or 50 metres of a borehole or well will<br />
have to comply by 1 April 2008.<br />
3. Remaining existing tanks will have to comply by 1 April 2010.<br />
Key differences between Regulations in Scotland and England<br />
The requirements of the Regulations can differ with the following key differences:<br />
1. Regulations in Scotland apply to domestic storage above 2500 litres. The Oil Storage<br />
Regulations England apply to domestic oil storage with over 3500 litre capacity.<br />
2. Regulations in Scotland apply to storage of waste oil and oil stored on farms. The storage<br />
of waste mineral oils is exempt under the Oil Storage Regulations England as their storage<br />
is covered by the Waste Management Licensing regulations 1994.<br />
3. Regulations in Scotland apply to storage of oil in buildings. The Oil Storage Regulations<br />
England exempts the storage of oil within a building.<br />
4. Regulations in Scotland exempt oil stored in accordance with a Part A authorisation /<br />
permit under the Pollution Prevention and Control (PPC) Regulations 2000, or the<br />
Environmental Protection (Prescribed Processes and Substances) Regulations 1991and<br />
premises used as an oil distribution depot for the onward distribution of oil to other places.<br />
The Oil Storage Regulations England exempt storage of oil at premises used for refining oil<br />
or for the onward distribution of oil to other places.<br />
1 The storage of oil as specified in the Water Environment (Oil Storage) (Scotland) Regulations<br />
2006 is a controlled activity within the meaning detailed in the Water Environment (Controlled<br />
Activities) (Scotland) Regulations 2005. The controlled activity of storage of oil is deemed to be<br />
authorised (under a general binding rule) if it is carried on is accordance with the appropriate<br />
provisions of the Water Environment (Oil Storage) (Scotland) Regulations 2006.
Environment Alliance - working together<br />
Pollution Prevention Guidelines<br />
Works and maintenance in or near water: PPG5<br />
PPG5<br />
October 2007<br />
These guidelines are produced jointly by the Environment Agency for England and Wales, the Environment and<br />
Heritage Service for Northern Ireland and the Scottish Environment Protection Agency, referred to here as we or us.<br />
These guidelines cover construction and maintenance works in, near or liable to affect surface waters and<br />
groundwaters.<br />
Surface waters include rivers, streams/burns, dry ditches, lakes/lochs, loughs, reservoirs, ponds, canals,<br />
estuaries and coastal waters.<br />
Groundwater is all water below the surface of the ground in the saturation zone and in direct contact with the<br />
ground or subsoil.<br />
You should consider these guidelines on a site by site basis, and we advise you to consult us for help. You can<br />
find contact details at the end of these guidelines.<br />
Pollution Prevention Guidelines (PPGs) are based on relevant legislation and good practice. They will help you<br />
manage your environmental responsibilities and protect the environment.<br />
Following these guidelines doesn t remove your responsibility to comply with the law and prevent pollution.<br />
If you cause or allow pollution you may be committing a criminal offence. It is in the operator s interest to<br />
follow the PPGs because they constitute current best practice and following them will minimise threat to the<br />
environment.<br />
1. Introduction<br />
1.1 Legal requirements<br />
Your construction and maintenance activities in or near water have the potential to cause serious pollution or<br />
impact on the bed and banks of a watercourse and on the quality and quantity of the water. Some activities with<br />
the potential for affecting watercourses or groundwater may require either consent in England and Wales under<br />
the Water Resources Act 1991 or an authorisation in Scotland under the Water Environment (Controlled Activities)<br />
(Scotland) Regulations 2005 (also referred to as CAR) - see reference 1. In Scotland depending on the nature of the<br />
activity there are three levels of authorisation.<br />
Types of activity that may impact upon the bed and banks of a watercourse or of a wetland include:<br />
repairs, maintenance or improvements to any structure in , over or above main river ( as defined in the Water<br />
Resources Act 1991 )<br />
erection or construction of any structure, either permanent or temporary, in, over or above main river<br />
diversion of flows<br />
works within the river channel or a lake/loch<br />
works within the vicinity of a river, or loch or wetland (in Scotland)<br />
any works likely to increase the risk of flooding<br />
works within 10.0metres of a Main River watercourse or flood defence (in England, Northern Ireland and Wales).<br />
There may be local variations in this distance e.g. in Environment Agency Midlands region it is 8.0 metres.<br />
Contact us at the planning stage of your project to confirm this.<br />
PPG 5 page 1
PPG 5 page 2<br />
Types of activity that have the potential to cause pollution of groundwater include:<br />
use of potentially polluting substances near groundwater abstraction boreholes (within Source Protection<br />
Zones in England and Wales, and within 50 metres in Scotland)<br />
use of potentially polluting substances near wells and springs<br />
use of potentially polluting substances in areas where groundwater is vulnerable, e.g. high groundwater table<br />
and thin covering soil<br />
sub-water table construction using materials containing potential pollutants (in Scotland)<br />
Types of activity that may remove water from sensitive parts of the water environment or affect other water users<br />
include:<br />
dewatering of excavations, particularly abstraction of large amounts of groundwater<br />
You should contact us early on in your project as the time-scale for obtaining consent or authorisation for these<br />
activities can take up to four months from receipt of the application. Check the NetRegs website - see web site<br />
list- for information on your legal environmental obligations; in Scotland, read also references 2 and 3.<br />
1.2 <strong>Planning</strong><br />
Most pollution incidents are avoidable. With careful planning you can reduce the risk of your work causing<br />
pollution. Most of the measures needed to prevent pollution cost very little, especially if they are included at<br />
the planning stage of any scheme or project. We suggest the following framework for managing environmental<br />
hazards on your site; some of the items may be legal requirements.<br />
Write and implement<br />
an environmental<br />
management<br />
plan reference 8<br />
to include waste<br />
management<br />
section 7 and<br />
incident response<br />
section 8<br />
reference 9<br />
Continually monitor<br />
and review the<br />
environmental<br />
impact of your work<br />
and update your<br />
management plan<br />
as necessary<br />
Use sustainable<br />
drainage systems<br />
(SUDs) as part of<br />
your design and<br />
construction control<br />
measures section<br />
2.2a and references<br />
6 & 7<br />
Identify all<br />
interested<br />
groups e.g.<br />
Regulators, Local<br />
Authorities, nature<br />
conservations<br />
bodies, sewerage<br />
providers<br />
Plan to protect your<br />
Environment<br />
Carry out a full<br />
Environmental<br />
Impact Assessment<br />
(** See reference<br />
below)<br />
* Some examples of site specific environmental hazards and sensitivities:<br />
oil or chemical pipelines<br />
mains water supply pipelines<br />
high voltage fluid filled cables<br />
downstream abstractors<br />
high amenity areas<br />
fish farms<br />
sensitive habitats e.g. wetlands<br />
Identify your legal<br />
obligation and what<br />
permissions/<br />
authorisations<br />
you need. These<br />
can take up to four<br />
months to issue<br />
Identify any special<br />
procedures or<br />
control measures<br />
to protect the<br />
environment<br />
Identify all<br />
site specific<br />
environmental<br />
hazards and<br />
sensitivities<br />
(*See list below)<br />
** Environmental impact assessments may be a legal requirement of your project as part of the planning process.<br />
You should contact your Local Authority planning department for advice on this part of your project. In England
see the Communities and Local Government web site and reference 4; in Scotland see reference 5 or it s<br />
update and Appendix 8 of reference 4<br />
Reference 8 covers many of the above points in detail.<br />
You can get information on local surface and groundwater water sensitivity from us before you start any work.<br />
In addition to preventing pollution of surface waters and groundwaters you should take precautions to prevent<br />
blocking of channels and culverts, and erosion of the riverbank or bed. This information should form part of the<br />
environmental impact assessment and site management plan.<br />
1.3 Pollution prevention<br />
If you cause pollution you will be responsible for the cost of the clean up. This can be expensive particularly if<br />
groundwater has become contaminated. There may be additional costs associated with our incident response<br />
and/or fines through the criminal courts or civil claims.<br />
Following these good practice guidelines will help you reduce the likelihood of an incident. If one does occur<br />
contact us immediately on our hotline number 0800 80 70 60. A rapid response to incidents will help to minimise<br />
the environmental impact and could reduce your overall costs - see section 8 and reference 9.<br />
Potential pollutants from your type of works could include:<br />
silt - section 2<br />
cement and concrete - section 3<br />
chemicals and solvents -section 4<br />
bridge cleaning debris - section 5<br />
herbicides - section 6<br />
waste materials (including hazardous waste or special waste in Scotland) - section 7<br />
Our PPG6 guidance document covers construction and demolition sites -reference 10. Also, the NetRegs website<br />
- web site list - has guidance, specific for the Construction sector, on environmental regulations and good practice.<br />
You should check these references to find the information that applies to your project.<br />
2. Silt<br />
Silt pollution is a major cause of environmental incidents. It can damage and kill aquatic life by smothering and<br />
suffocating and can cause flooding by blocking culverts and channels.<br />
2.1 Activities that can cause silt pollution<br />
Disturbance of river<br />
bed or bank<br />
De watering and<br />
pumping<br />
of excavations<br />
Silt and<br />
contaminated water<br />
can be caused by<br />
Run off from<br />
exposed ground<br />
Plant washing<br />
Roads and river<br />
crossings<br />
Section 2.1 a Section 2.1b Section 2.1c Section 2.1d<br />
If you can prevent water becoming contaminated in the first place, then it reduces the risk of pollution and the<br />
overall cost of your control measures. To avoid silt pollution you should, wherever possible, use methods of work<br />
that reduce or eliminate working in the channel and that do not contaminate surface water.<br />
PPG 5 page 3
PPG 5 page 4<br />
2.1a Disturbance of the river bed / working in the river channel<br />
When you have considered all other options and working in the channel is still necessary, such as in dredging<br />
operations, contact us as early as possible in your planning stages to discuss appropriate pollution control<br />
measures. Permission for this type of work may take up to four months to obtain. The risk of silt pollution causing<br />
an incident will depend on many factors including: -<br />
likelihood of silt being disturbed<br />
what the river bed is made of, e.g. silt or gravel<br />
the conditions in which the work is carried out, e.g. hot weather and low flows<br />
Silt pollution caused by working in surface waters can be minimised or prevented by keeping water out of the<br />
works area using appropriate isolation techniques, such as coffer dams and by-pass channels.<br />
2.1b Disposal of water from excavations, dewatering and pumping<br />
Problems with disposal of water from the above activities may be minimised or avoided by:<br />
preventing water from entering excavations, by using cut off ditches<br />
considering the impact on groundwater if you use well point dewatering or cut off walls<br />
using pump sumps in excavations<br />
supporting inlet hoses above the bed<br />
discharging on to hard surfaces (concrete slabs/gravel) in to surface waters<br />
use of appropriate pump rates to avoid disturbance of bed or bank the maximum rate should be set after<br />
consideration of the flow of the river, the location of the discharge and the risk of erosion<br />
protection of the pump inlet to avoid drawing in aquatic life and other debris<br />
minimising disturbance of standing water<br />
2.1c Exposed ground and stockpiles<br />
Soil stripping and vegetation removal at the start of a project can increase the volume of contaminated surface<br />
water run-off. It can also reduce the area of vegetated land available for disposal of silty water.<br />
You should:<br />
minimise the amount of exposed ground and soil stockpiles from which the water drains and the period of time<br />
such water drains this is also a legal requirement in Scotland (see General Binding Rules in reference 1)<br />
only remove vegetation from the area that needs to be exposed in the near future<br />
seed or cover stockpiles<br />
use silt fences at the toe of the slope, made from geotextiles, to reduce silt transport<br />
collect run-off in lagoons and allow suspended solids to settle before disposal - reference 3<br />
2.1d On-site working<br />
The movement and maintenance of plant on site can generate silt and oil contaminated water. Sources of silt such<br />
as plant and wheel washing and site roads and river crossings carry a high risk of causing pollution.<br />
Plant and wheel washing<br />
To reduce the pollution risk make sure that:<br />
plant and wheel washing is carried out in a designated area of hard standing at least 10 metres from any<br />
watercourse or surface water drain<br />
run-off is collected in a sump - recycle and reuse water where possible<br />
settled solids are removed regularly<br />
discharge of contained water goes to foul sewer (if possible) with prior permission from your local sewerage<br />
provider section 2.2e - or<br />
tanker off site for authorised disposal section 2.2f
Site roads and river crossings<br />
Run off from site roads and river crossings can contain high levels of silt. Reduce the pollution risk by:<br />
brushing or scraping roads to reduce dust and mud deposits<br />
putting small dams in artificial roadside ditches to retain silt<br />
using existing permanent bridges or pipe crossings for river crossing<br />
if necessary building temporary bridges - but not fording rivers<br />
working from the bank where possible not in the river<br />
2.2 Disposal of contaminated water - treatment and disposal methods<br />
Where run off water is contaminated with silt or other pollutants such as oil this water must not be pumped or<br />
allowed to flow directly or indirectly in to surface waters or groundwater without treatment.<br />
If a discharge to surface waters, groundwater, soakaways or surface water sewers is necessary it may require<br />
consent or authorisation from us. Contact us early in the planning stage of your project as a consent or<br />
authorisation could take up to four months to issue. If we issue a consent or authorisation it will limit volume,<br />
amount of silt and the presence of any oil in the discharge, and may have conditions for additional substances.<br />
The choice of method for the treatment and disposal of contaminated water will depend on:<br />
the volume of water<br />
the area of land available for storage, treatment or discharge<br />
the amount and type of silt<br />
the presence of other substances in the water<br />
the conditions of any consent or authorisation<br />
Treatment and disposal methods include:<br />
Tanker off site<br />
Section 2.2f<br />
Discharge to sewer<br />
Section 2.2e<br />
Sustainable<br />
Drainage Systems<br />
(SUDS) Section 2.2a<br />
Contaminated<br />
Water treatment and<br />
disposal<br />
Pump to grassland<br />
Section 2.2d<br />
Settlement Lagoons<br />
Section 2.2b<br />
Filtration<br />
Section 2.2c<br />
PPG 5 page 5
PPG 5 page 6<br />
2.2a Sustainable Drainage Systems (SUDS)<br />
Sustainable drainage is the practice of controlling surface water runoff as close to its origin as possible by<br />
slowing flows, allowing adequate settlement and biological action to take place before water is discharged to a<br />
watercourse or to ground. It uses softer engineering solutions to imitate natural drainage rather than traditional<br />
piped drainage solutions. Sustainable drainage methods used both in the construction phase and in the design<br />
of the project will:<br />
reduce flood risk from development within a river catchment<br />
minimise diffuse pollution arising from surface water runoff<br />
minimise the risk of pollution to groundwater<br />
minimise environmental damage, such as bank erosion and damage to habitats<br />
maintain or restore the natural flow regime of the receiving watercourse<br />
maintain recharge to groundwater<br />
achieve environmental enhancements, improvement to wildlife habitats, amenity and landscape quality<br />
Some examples of source control methods are shown in the following list:<br />
Examples of source control sustainable drainage systems<br />
Porous surface pavements water permeates through in to the soil or sub-surface reservoir which can then<br />
be allowed to discharge slowly rather than directly running off. This will minimise the volume of water that<br />
you might need to treat and can also recharge groundwater. Porous pavements need to be protected during<br />
installation from blocking by excessive silt contaminated water.<br />
Infiltration trenches a shallow excavated trench backfilled with stone to make an underground reservoir. Run<br />
off is diverted in to the trench and then filters in to the subsoil. The closer to the source the more effective this<br />
method will be.<br />
Infiltration basins a shallow surface impoundment where water is stored until it gradually infiltrates in to the<br />
soil of the basin floor. The performance of the basin depends largely on the permeability of the soil and the<br />
depth of the water table<br />
Filter drains or French drains - these are similar to infiltration trenches but also allow movement of run off<br />
slowly towards a watercourse allowing time for filtration, storage and some loss of water due to evaporation /<br />
infiltration.<br />
Swales grassed wide shallow depressions which lead water overland from a drained surface in to storage or<br />
discharge system. They provide temporary storage for run off reducing high flows. Solids are retained and oily<br />
residues and organic matter broken down in the top layer of the soil and vegetation.<br />
Filter strips vegetated sections of land designed to accept run off as an overland sheet flow. To be effective<br />
they should be 5 15 metres wide and are best employed on the upstream end of a drainage system. They are<br />
most effective at removing excess solids and pollutants before discharging to downstream system.<br />
Other SUDS can be considered including ponds, detention basins (dry ponds) and wetlands.<br />
At the planning stage of your project consider how your drainage can be managed by using SUDS. Pollution<br />
removal by these methods is achieved by sedimentation, adsorption, absorption, filtration and microbial action.<br />
In Scotland, discharges of water run-off from construction sites are required to be treated by either a Sustainable<br />
Urban Drainage System (SUDS) or an equivalent equipped to avoid pollution. However, the final SUD System<br />
cannot be an equivalent and must be a recognised SUD System (see General Binding Rule 10 in reference 1).<br />
For more information on SUDS see the CIRIA website in the websites list and references 6 and 7.
2.2b Settlement lagoons or tanks<br />
To be effective a settlement lagoon or tank should retain contaminated water long enough for silt to settle<br />
out. The length of time will depend on the type of silt, with finer clay solids taking longer to settle . If you use<br />
flocculants to aid settlement you must discuss this option with us before use. Flocculants can themselves be<br />
polluting and/or toxic and need careful use and monitoring to be effective. The checklist below gives guidance on<br />
lagoon/tank operation.<br />
Table 1 gives guidance on the volume of lagoon or tank needed for a three-hour settlement at a defined rate of<br />
inlet discharge.<br />
Typical dimension of a settlement lagoon / tank for a three hour settling time<br />
Pump Diameter Discharge rate in to the lagoon Length Width<br />
6 inch pump 3000 l/min 60m 20m<br />
6000 l/min 80m 27m<br />
4 inch pump 1000 l/min 30m 10m<br />
2500 l/min 50m 17m<br />
Assuming a tank / lagoon depth of 1 m , where length = three times the width<br />
Table 1: Settlement pond dimensions - the size of the tank/lagoon is determined by the rate of introduction of<br />
water .<br />
Settlement lagoon / tank a checklist<br />
maintain a constant pumped inlet rate<br />
minimise the inlet flow as much as possible by using energy dissipaters or rip rap<br />
position inlet pipe work vertically to dissipate energy<br />
provide lined inlet chamber to reduce velocity of flow<br />
line the inlet chamber and outlet weir with materials like geotextiles , brickwork ,polythene or timber<br />
have a long outlet weir to minimise disturbance<br />
two or three lagoons in series will increase silt retention<br />
clean inlet chamber regularly<br />
monitor discharge quality frequently<br />
See reference 8 for more detail.<br />
2.2c Filtration<br />
If you do not have the space for lagoons and the water is contaminated with course silt you may be able to use<br />
tanks filled with filter material. Single sized aggregates 5 10 mm, geotextiles or straw bales can be used as a<br />
filter. You must monitor carefully the inlet pump rate and discharge quality.<br />
2.2d Pump to grassland<br />
You must have our permission and the landowners before planning to use this method of disposal. The discharge<br />
rate must match the rate of infiltration in to the soil which will vary with the type soil, amount of vegetation cover<br />
and the gradient.<br />
2.2e Discharge to sewer<br />
If discharge to a foul sewer is possible you will require the permission of the local sewerage provider. You should<br />
approach them at an early stage in the project. They may issue a consent/authorisation limiting the volume and<br />
content of the discharge.<br />
PPG 5 page 7
PPG 5 page 8<br />
2.2f Tanker off site<br />
If no other disposal routes are available then contaminated water can be collected and disposed off site by tanker.<br />
This may be a costly option and must be discussed with us at the planning stage of your project.<br />
3. Concrete and cement<br />
Fresh concrete and cement are very alkaline and corrosive and can cause serious pollution. Concrete and cement<br />
mixing and washing areas should:<br />
be sited 10 metres from any watercourse or surface water drain to minimise the risk of run off entering a<br />
watercourse<br />
have settlement and re-circulation systems for water reuse, to minimise the risk of pollution and reduce water<br />
usage<br />
have a contained area for washing out and cleaning of concrete batching plant or ready mix lorries; see section<br />
2.1d above<br />
collect wash waters and, where necessary, discharge to the foul sewer (you must have permission from the<br />
local sewerage undertaker for this), or contain wash water for authorised disposal off site<br />
Wash waters from concrete and cement works should never be discharged in to the water environment.<br />
4. Oil and chemicals<br />
In England, oil storage containers (e.g. tanks, IBCs, drums and mobile bowsers) greater than 200 litres must<br />
comply with the Control of Pollution (Oil Storage) (England) Regulations 2001 - reference 11. Similar legislation is<br />
expected in Northern Ireland.<br />
In Scotland, storage must be compliant with the Water Environment (Oil Storage) (Scotland) Regulations 2006<br />
- reference 12 -; these regulations apply to the storage of any volume of any kind of oil, with more prescriptive<br />
requirements applying to industrial, commercial and institutional sites storing over 200 litres of oil.<br />
4.1 Storage - general<br />
Make sure fuel, oil and chemical storage on site is secure. Site the storage on an impervious base within a<br />
secondary containment system such as a bund. The base and bund walls should be impermeable to the material<br />
stored and able to contain at least 110% of the volume stored. Site the storage area above any flood water level<br />
and where possible away from high-risk locations (such as within 10 metres of a watercourse or 50 metres of<br />
a well, borehole or spring), to minimise the risk of a spill entering the water environment. Detailed guidelines<br />
concerning above ground oil storage tanks can found in our guidance PPG2 - reference 13 - and in PPG 26<br />
reference 14.<br />
Keep a spill kit with sand, earth or commercial products that are approved for your stored materials, close to your<br />
storage area. Train staff on how to use these correctly.<br />
Remove damaged leaking or empty drums from site immediately and dispose any drums via a registered waste<br />
disposal contractor
4.2 Security<br />
You should secure your site against theft and vandalism. Statistics show that damage from vandalism is a<br />
common cause of pollution. You can t use vandalism as a defence if you are taken to court because of a pollution<br />
incident<br />
Therefore take action to secure your site by<br />
fitting lockable valves and trigger guns on pipework from storage containers<br />
installing anti siphon valves in pipework between containers and pumps<br />
installing armoured hoses<br />
storing tanks drums and mobile bowsers in a locked container or compound when not in use<br />
considering lighting, alarm or CCTV systems for your site or compound<br />
installing lockable fencing around the site or employing security staff<br />
4.3 Refuelling<br />
The risk of spilling fuel is at its greatest during refuelling of plant. To minimise this risk:refuel<br />
mobile plant in a designated area, on an impermeable base away from drains or watercourses<br />
use a bunded bowser<br />
supervise all refuelling and bulk deliveries<br />
check the available capacity in the tank before refuelling<br />
don t jam open a delivery valve<br />
check hoses and valves regularly for signs of wear<br />
turn off valves after refuelling and lock them when not in use<br />
position drip trays under pumps to catch minor spills<br />
keep a spill kit with sand, earth or commercial products for containment of spillages<br />
provide incident response training to your staff and contractors<br />
4.4 Biodegradable oils<br />
If possible use biodegradable chainsaw chain bar lubricant and biodegradable hydraulic oil in plant when working<br />
in or near watercourses. The Environment Agency and its contractors use biodegradable oils for their own<br />
operations. Biodegradable oils are less toxic than most of the synthetic oil but should still be stored and used to<br />
the same standards as other oils.<br />
4.5 Trade materials<br />
Sealant, coatings, adhesives and glazings can be toxic to plants and animals if released in to the environment.<br />
Select, store and use these materials carefully to save resources and protect the environment. You must not use<br />
sealant and glazing compounds containing asbestos. You should<br />
use water based or low solvent products<br />
avoid products containing lead as a drying agent and those containing hazardous solvents (toluene or<br />
chlorinated hydrocarbons )<br />
provide safe and secure storage<br />
For guidance on general storage see our Pollution Prevention Pays. Getting your site right pack and DVD -<br />
reference 15.<br />
PPG 5 page 9
PPG 5 page 10<br />
5. Bridge maintenance and structures over water.<br />
Work to maintain bridges or other structures over or next to watercourses has a high risk of causing pollution. The<br />
maintenance work itself may require authorisation from us and you should contact us at an early stage in your<br />
plans to agree the most appropriate method of working and to agree an environmental management plan.<br />
You may need authorisations if the bridge crosses a main river. Contact us prior to starting your work to confirm<br />
this.<br />
5.1 Pollutant containment<br />
Dust, debris and wastewater are the most common pollutants produced by structure maintenance. You should<br />
choose a containment system designed to reduce the risk of pollution from your work. The system should take<br />
account of the sensitivity of the environment. The type of containment you need will depend on the sensitivity of<br />
the site.<br />
<strong>Method</strong>s of containment include:<br />
air or water impenetrable walls<br />
rigid or flexible framing lined as necessary<br />
fully sealed joints<br />
airlocks or resealable entryways<br />
negative air pressure (achieved by forced or natural air flow) and<br />
exhaust air filtration<br />
In sealed containment areas you should provide filtered ventilation to prevent the build-up of dust and minimise<br />
the possibility of air escaping through breaches of the containment.<br />
Use physical cleaning instead of liquid chemicals such as caustic and acid solutions. Contain wastewaters from<br />
surface washings and agree the disposal method with us as part of the environmental management plan before<br />
you start work. In some circumstances, you may be able to use a barge with a wastewater containment facility for<br />
working over water, or dispose to foul sewer with prior permission of the local sewerage undertaker. You should<br />
contact us early on in the planning stages of the project so we can advise on pollution prevention methods.<br />
The containment facility must be designed so that the structure does not obstruct the river flow beneath it to such<br />
an extent that it increases the risk of flooding to an unreasonable level.<br />
5.2 Paint removal<br />
Paint removal methods include:-<br />
abrasive blast cleaning<br />
blasting in a closed circuit<br />
preparation by various types of wet abrasive blasting or water jetting<br />
chemical stripping and<br />
hand or power tool cleaning<br />
Abrasive blasting produces the greatest level of dust and debris. The use of vacuum attachments on power tools<br />
can reduce dust generation. Water cleaning methods produce less debris, but generate run-off, which needs to be<br />
contained and treated. We can advise you on the best method of treatment.<br />
Sample existing coatings for hazardous materials (e.g. lead) before starting to remove them. This can help<br />
determine the level of containment you will need. The level of containment needed depends on:<br />
the amount of paint to be removed<br />
the type and concentration of the hazardous materials<br />
the sensitivity of the surrounding environment
5.3 Surface cleaning<br />
If you are using high-pressure water or steam cleaners see our guidance in PPG 13 - reference 16 - before starting<br />
work. You should avoid using grit blasting with slag-derived grit as they can contain significant levels of heavy<br />
metals such as copper. These can be toxic if they get in to the water environment. Reduce the potential for<br />
contamination by using garnet, low silica abrasive or recycled glass media with vacuum attachments.<br />
5.4 Painting<br />
Our advice for painting is much the same as for paint removal although the volume of waste and size of operations<br />
will be less. Remove dust and debris by sweeping or vacuum cleaning before painting. Paints can be applied onsite<br />
using brush, conventional spray or airless spray. Consider using electrostatic spray units to reduce the loss of<br />
product by over-spraying.<br />
Carefully consider the type of paint you use. Although water based solvent free paints have lower environmental<br />
impact they may require more frequent application. Solvent-based paints could have a higher environmental<br />
impact but will last longer and require less maintenance. The decision to use water or solvent-based paints<br />
should be based on the environmental sensitivity of the area/surrounding environment and ease of access to the<br />
structure.<br />
6. Herbicide use<br />
In England, Northern Ireland and Wales you must have our written approval to use herbicides in or near waters.<br />
This takes two weeks from the date we receive the application. Only approved herbicides may be used, and<br />
only by authorised contractors. If approval is given you, as the applicant, and the contractor are responsible for<br />
ensuring that the interests of other river users are not adversely affected.<br />
In Scotland, aerial application of herbicides in or near the water environment needs approval from us; also, you<br />
should consult with us on any other application of herbicide in or near the water environment, as pollution caused<br />
by such herbicide use will be deemed an unauthorised activity and enforcement action may be taken against the<br />
person responsible.<br />
PPG 5 page 11
PPG 5 page 12<br />
7. Waste management<br />
Legal waste storage and disposal are essential for effective pollution prevention.<br />
Under the Duty of Care - reference 17 - you have a legal duty to make sure any waste you produce does not escape<br />
from your control. Waste must be transferred to an authorised registered or exempt waste carrier or waste<br />
manager. It must be accompanied by a full description of the waste and a waste transfer note and be disposed of<br />
lawfully.<br />
Hazardous wastes, or special wastes in Scotland, such as oily wastes, acids, solvents and solvent-based products,<br />
have particular legal requirements and their movement must be accompanied by a consignment note - reference<br />
18. Everyone involved in the transfer of the waste, including us, must keep copies of the consignment notes for<br />
proof of legal disposal.<br />
If you are a hazardous waste producer located in England or Wales you must register with the Environment Agency<br />
as a Hazardous Waste Producer. For further advice contact us on 08708 502 858 or go to our web site. There is no<br />
such requirement in Northern Ireland or Scotland.<br />
Find out how these waste regulations affect your site. Check the Guidance by Environmental Topic section of the<br />
NetRegs website (in web site list) for information on waste legislation and how you can comply. In Scotland see<br />
also reference 19.<br />
Draw up a site waste management plan.<br />
Site waste management plan checklist<br />
Carry out a waste minimisation audit to identify where you can reduce the volume of waste you produce -<br />
contact Envirowise for free advice, on 0800 585794 or using its website (see websites list below)<br />
Reuse materials or use products that can be reused many times<br />
Substitute materials for less hazardous ones e.g biodegradable lubricants and water based paints<br />
Recycle waste where possible In England, Northern Ireland and Wales contact your local council or waste<br />
contractor for recycling facilities. In Scotland in the first instance check the Waste Awareness website (www.<br />
wasteawarebusiness.com) to identify waste recycling facilities in your area. Also contact your local council,<br />
waste contractor, or the Scottish Industrial Symbiosis Programme (www.nisp.org.uk/)<br />
Segregate different wastes for recycling, hazardous waste and general waste and label them. Do not mix or<br />
dilute hazardous wastes<br />
Store waste in suitable containers of sufficient capacity to avoid loss, overflow or spillage<br />
Store waste in designated areas, isolated completely from surface water drains and areas which discharge<br />
directly to the water environment.<br />
Cover or enclose skips unless they are stored undercover or within a building.<br />
Take waste off your site frequently; do not allow large quantities to accumulate.
8. Incident response<br />
You should immediately report to us any incidents that have had or that could have had an environmental impact.<br />
Use our hotline number 0800 80 70 60 to report all incidents.<br />
Incidents include spillages (oils and chemicals), contaminated run-off, flooding, riverbed disturbance, damage to<br />
underground services, damage to habitats, poor waste disposal and storage. If in doubt report it.<br />
You should produce an Incident Response Plan as part of the environmental impact management of your work.<br />
Include the following: -<br />
list of key external and internal contacts<br />
reporting procedures<br />
site plan including drainage and location of storage/refuelling areas<br />
list of stored materials<br />
details of local environmental sensitivities, e.g. abstractors, high amenity areas and fish farms<br />
location of spill equipment<br />
procedures for spill containment and remediation<br />
Train your staff and contractors in the use of spill equipment and how to manage and dispose of waste materials<br />
legally.<br />
If you are using oil and chemicals in close proximity to a watercourse, store a suitable spill kit or absorbent<br />
materials nearby. Provide appropriate temporary storage for any oils and chemicals. Contain all spillages using<br />
absorbents such as sand, soil or commercially available booms or pads and notify us immediately, using the<br />
emergency hotline number above.<br />
For full guidance on Incident Response planning use our PPG 21 - reference 9.<br />
PPG 5 page 13
PPG 5 page 14<br />
9. References<br />
All the Pollution Prevention Guidance notes (PPGs) are available at:<br />
- www.environment-agency.gov.uk/ppg<br />
- www.sepa.org.uk/guidance/ppg<br />
You can also order the Pollution Prevention Pays pack at the first of these sites.<br />
1. The Water Environment (Controlled Activities) (Scotland) Regulations 2005 A Practical Guide. SEPA 2007<br />
in SEPA website and in print version obtainable from SEPA.<br />
2. Prevention of Pollution from Civil Engineering Contracts; Special Requirements (SG 31). SEPA 2006 - in<br />
SEPA website.<br />
3. Prevention of Pollution from Civil Engineering Contracts Guidelines for Special Requirements (SG-32).<br />
SEPA 2006.<br />
4. Environmental Impact Assessment: Guide to Procedures. Department for Communities and Local<br />
Government. ISBN 0 72 772960 8<br />
5. The Environmental Impact Assessment (Scotland) Regulations 1999, Circular 15/1999 in Scottish<br />
Government website.<br />
6. The SUDS Manual. CIRIA C697. ISBN 0 86017 697 5<br />
7. Site Handbook for the Construction of SUDS. CIRIA C698. ISBN 0 86017 698 3.<br />
8. Environmental Good Practice on Site . CIRIA C502 1999. ISBN 0 86017 502 2<br />
9. PPG21: Pollution Incident Response <strong>Planning</strong>.<br />
10. PPG 6: Working at Construction and Demolition sites.<br />
11. Guidance note for the Control of Pollution (Oil Storage) (England) Regulations 2001 in Defra website and<br />
in print.<br />
12. Guidance note for the Water Environment (Oil Storage) (Scotland) Regulations2006 Scottish Government<br />
in Scottish Government website and in print.<br />
13. PPG2: Above Ground Oil Storage Tanks.<br />
14. PPG26: Storage and Handling of Drums and Intermediate Bulk Containers.<br />
15. Pollution Prevention Pays. Getting your Site Right Industrial and Commercial Pollution Prevention. in<br />
Environment Agency website.<br />
16. PPG 13: Vehicle Washing and Cleaning.<br />
17 Waste Management, The Duty of Care, A Code of Practice (Revised 1996). The Stationary Office. ISBN 0<br />
11- 753210X.<br />
18. Hazardous Waste (England and Wales) Regulation 2005 Statutory<br />
Instrument 2005 No 894. ISBN 0 110726 855<br />
Hazardous Waste (Northern Ireland) Regulations 2005, SR 300. ISBN 0 33796 064 X<br />
Special Waste Regulations 1996, SI972. ISBN 0 11 054565 6<br />
Special Waste Amendment (Scotland) Regulations 2004, SSI 112. ISBN 0 11069 0303
19. The Small Environmental Guide for Construction Workers. SEPA and CIRIA 2006 in SEPA website and in<br />
paper version obtainable from SEPA<br />
Websites<br />
Environment Agency: www.environment-agency.gov.uk<br />
Environment and Heritage Service for Northern Ireland: www.ehsni.gov.uk<br />
Scottish Environment Protection Agency: www.sepa.org.uk<br />
Department for Environment Food and Rural Affairs: www.defra.gov.uk<br />
Communities and Local Government (England and Wales): http://www.communities.gov.uk/<br />
Scottish Government: http://www.scotland.gov.uk/<br />
Envirowise: www.envirowise.gov.uk<br />
NetRegs: www.netregs.gov.uk<br />
Construction Industry Re<strong>search</strong> and Information Association : www.ciria.org.uk<br />
PPG 5 page 15
PPG 5 page 16<br />
Our contact details<br />
Environment Agency<br />
www.environment-agency.gov.uk<br />
HEAD OFFICE<br />
Rio House<br />
Waterside Drive<br />
Aztec West<br />
Almondsbury<br />
Bristol BS32 4UD<br />
Tel: 01454 624 400<br />
Fax: 01454 624 409<br />
Scottish Environment Protection Agency<br />
www.sepa.org.uk<br />
CORPORATE OFFICE<br />
Erskine Court<br />
The Castle Business Park<br />
Stirling FK9 4TR<br />
Tel: 01786 457 700<br />
Fax: 01786 446 885<br />
Environment and Heritage Service<br />
www.ehsni.gov.uk<br />
HEAD OFFICE<br />
17 Antrim Road<br />
Lisburn<br />
County Antrim BT28 3AL<br />
Tel: 028 9262 3100<br />
Fax: 028 9267 6054<br />
In England and Wales please contact your Local Development Control team through National Customer Contact<br />
Centre (NCCC) on 08708 506 506 or at enquires@environment-agency.gov.uk for details on any of the topics<br />
covered in this document.<br />
Environment first: This publication is printed on paper made<br />
from 100 per cent previously used waste. By-products from<br />
making the pulp and paper are used for composting and fertiliser,<br />
for making cement and for generating energy.<br />
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