Dr Bill Baker of the Environment Agency outlines the main
components of its new guidance document for the safe development
of housing on contaminated land
For many years, successive governments have recognised the need
to tackle the problems of regeneration of the large tracts of derelict
land in our urban areas - a legacy of our industrial past. There
have been many successful initiatives which have transformed some
of the most difficult sites into new developments for industrial,
commercial and residential purposes, which are an important part
of our modern communities.
On occasion, however, the reclamation and redevelopment of contaminated
sites has been constrained by an atmosphere of uncertainty, leading
to mistrust by the end user and the local community. There has also
been a lack of enthusiasm on the part of some developers to get
involved in developments involving expensive remediation, and concern
about the extent of residual liabilities should things go wrong.
This situation has had an adverse effect on the progress of the
Government's "brownfield" housing initiative, which is
intended to promote the regeneration of urban and inner city areas
and reduce the pressures on the progressive development of the countryside.
The Urban White Paper1 and the Spending Review 20002 have set a
target that 60 per cent of new housing should, by 2008, be provided
on previously developed land and through the conversion of existing
buildings. Furthermore, a target for the rate of reclamation of
brownfield land has been set to exceed 1,100 hectares per annum
by 2004. This should have the effect of reclaiming 5 per cent of
current brownfield sites by 2004, rising to 17 per cent by 2010.
Such challenging targets mean that we must seek to overcome many
of the barriers to redevelopment which currently exist.
FACING THE CHALLENGE
There are many barriers to the achievement of this target, often
associated with inconsistent application of technical guidance and
regulation. Primary control of the redevelopment process lies with
the planning authorities, the developer and their consultants. The
Environment Agency (EA) regulates remediation processes and is a
statutory consultee on planning applications. Therefore, the EA
has an indirect influence on the regeneration of brownfield land.
The problems of public perception of the risks associated with
living on a previously contaminated site arise from a general widespread
lack of understanding of the complex multidisciplinary problems
involved in the management of contaminated land and its remediation.
While the public cannot reasonably be expected to be aware of the
complexity of the subject, it is vital that regulators, developers,
contractors and consultants are fully aware of the issues. This
is not always the case, and can lead to major problems in developing
such land.
Recent research has revealed that most householders, both owners
and tenants, living on developed brownfield sites, were not aware
of their situation due to a reluctance on the part of housing associations,
local authorities, developers and builders to share this information.3
This can result in substantial concern to residents, when information
on the history of a site is released later in an uncontrolled way.
Significant social and economic disadvantage can be suffered by
a householder when the prospective purchaser's solicitor's questions
relating to the site's previous use and remediation cannot be satisfactorily
answered from the local authority records. In contrast, an open
policy on information provision has avoided such problems and led
to much smoother sale and insurance of properties.
Local authorities operate the planning regime and have relied upon
the use of the Interdepartmental Committee on the Reclamation of
Contaminated Land (ICRCL) Guidance, introduced over twenty years
ago in 1978.4 This provides "tentative" guideline trigger
values for the level of various contaminants in soil that can be
tolerated in the context of domestic housing and other sensitive
developments. The generally inconsistent and uncritical way in which
the "guidance" has been applied in the past has often
led to conflict between developers and regulators, with many instances
of over prescriptive remediation being demanded by the regulator
to ensure public safety. In contrast, there has sometimes been an
uncritical acceptance of the recommendations of the developers'
consultant for inexpensive but inadequate remediation which is not
sustainable and may become unsafe.
This overall situation emphasises the need for new technical guidance
for contaminated land, to assist those involved in the business
of house building and redevelopment of sites affected by contamination.
Such a programme of guidance has been in development for a period
of years and is nearing completion, with publication expected in
2001. While the planning regime remains the primary means of ensuring
that land contamination is dealt with properly when a change in
use is proposed, the year 2000 saw the introduction of the new Part
IIA regime for dealing with contaminated land where it is found
to be unsuitable for current use.5 This regime complements the planning
system, insofar as Part IIA deals with current use, and planning
with proposed changes in use.
One area of technical guidance which has already been published
in support of redeveloping brownfield sites is the new "Guidance
for the safe development of housing on land affected by contamination",
published in June 2000 jointly by the EA and the National House
Building Council (NHBC).10
THE NEW REGIME
The implementation of the new regulatory regime represented by Part
IIA of the Environmental Protection Act 1990 (introduced by the
Section 57 Provisions for the Regulation of Contaminated Land of
the Environment Act 1995)5 in April 2000, provides an effective
means of dealing with those sites which are not captured under planning,
primarily because no change in use is proposed. Its introduction
completes an effective framework for the remediation and control
of land contamination. It is based upon a sound set of principles,
which include: "suitable for use" standards of remediation;
the "polluter pays" principle for the allocation of liability;
the assessment of contamination by a risk based approach; and the
achievement of reasonable solutions, greater consistency and sustainability
through policies of consultation, co-operation and partnership.
The central theme of the new regime places great emphasis upon
a system of risk assessment subject to open scrutiny as promoted
in the associated statutory guidance.6 It is supported by a growing
volume of sound technical guidance on assessment, remediation, etc
from DETR and EA sponsored research. This will clearly lead to greater
consistency, the promotion of best practice, and a greater level
of confidence in the systems of remediation and their durable safety.
By following policies of openness and transparency, developers should
gain more widespread understanding and acceptance for brownfield
development by potential purchasers and householders.
Essential to underpin these changes in the future will be the development
of the "Model procedures for the management of contaminated
land".7 They incorporate existing good technical practice,
including the use of risk assessment and risk management techniques,
into a systematic framework for identifying, making decisions about
and taking appropriate action to deal with contamination, in a way
which is consistent with UK policy and legislation.
Tools have been developed to assist regulators and developers alike
in the difficult decision-making process. Among these is the Contaminated
Land Exposure Assessment (CLEA) risk assessment model.8 The CLEA
uses the toxicological information for particular contaminants,
information on the contaminant levels in soil, an analysis of the
potential pathways for a contaminant to cause harm to the human
condition in the sensitive context of domestic housing, and probability
theory to enable site specific risk assessment to be carried out.
Its most important application is the development of new more robustly
researched "guideline" values which will replace the old
ICRCL "tentative" figures.9
There are other sensitive targets, apart from housing, that will
also need to be evaluated for potential risk. They include the local
water environment, and tools have also been developed to assist
in the assessment of risk and the need for remediation. While the
new regulatory system applies primarily to the current state of
land, the basic principles of risk assessment are equally applicable
to all development situations and their application will ensure
successful and sustainable regeneration of brownfield land.
The local authority system of inspection of land, which is an integral
part of the new legislation, will provide the planners with much
valuable information which will help in avoiding the mistakes of
the past, whereby planning approval was often given for development
in ignorance of the potential problems of contamination.
HOUSING DEVELOPMENT GUIDANCE
The need for guidance specifically for the development of housing
on land affected by contamination was recognised some years ago
by the (then) DETR, following confirmation of the UK policy approach
to legislation in this area. A comprehensive guidance document was
drafted, which was based on the application of principles of the
risk assessment and management as advocated in the "Model procedures
for the management of contaminated land", the CLEA model and
other relevant guidance.
The volume of such guidance developed in recent years is formidable.
The EA, in close partnership with the NHBC, has reviewed this guidance
and, drawing from the relevant sources, has thereby developed a
used-friendly guidance document specifically designed for the use
of housing developers, house builders, housing associations, local
authorities, regulators and consultants. The objectives of the "Guidance
for the safe development of housing on land affected by contamination"
are:10
to support the brownfield housing initiative;
to overcome the wide inconsistencies in the application of
current guidance;
to overcome the problems of public perception and improve communication
of information; and
to point the developer and house builder and their advisors
towards appropriate solutions and best practice.
Within the guidance document, the "model procedures"
have been translated into a series of stages or steps in the process
of housing development, from initial consideration of a project
to the completion of remedial works and its validation. There are
eleven practical steps incorporated in the four main stages involving
the two phases of risk assessment, the evaluation and selection
of remedial measures, and the implementation of risk management,
as described below.
"Risk assessment" covers "hazard identification",
whereby a desk study and site reconnaissance is used to gather information
about previous contaminative uses and general physical and geological
conditions, so as to gain a preliminary understanding of potential
risks associated with the identification of the contamination likely
to be present on the site (steps 1 and 2).
This is followed by "hazard assessment", which involves
the identification of receptors and pollutant linkages likely to
exist on the proposed development, and may involve initial investigations
and analysis to provide a preliminary indication of the potential
for risks to health and the environment through the development
of a conceptual model (steps 3 and 4).
The "risk estimation" stage includes the design and execution
of a detailed investigation and analysis to collect sufficient data
to allow estimation of the risks that contaminants may pose to receptors,
eg residents under the conditions of the development (steps 5 and
6).
In the process of "risk evaluation" all available risk-based
information is reviewed to decide whether the estimated risks are
unacceptable, taking into account their nature and scale, and any
technical uncertainties which may be associated with the risk estimation
process (step 7).
The use of models and detailed guidance to assess the risks to
human health and other receptors such as controlled waters, ecological
systems and building structures and services, will be applicable
at this stage. The "evaluation and selection of remedial measures"
procedure covers the activities where decisions are made on the
most appropriate form of remedial measure to control or reduce unacceptable
risks. It involves the review of all available data to ensure that
there is sufficient information to carry out the evaluation and
selection process. Potentially suitable remedial options are then
identified, and the alternative options subjected to detailed analysis.
The preferred remedial strategy is then selected, based on the most
appropriate and cost effective of the available options (steps 8
and 9).
The "implementation of risk management action" involves
the design of the detailed development plan, submission along with
all supporting documentation to the approval authority, execution
of the remedial work and its post-development validation. There
may also be situations demanding long-term monitoring or maintenance
of certain measures which are vital to the on-going effectiveness
and durability of the development (steps 10 and 11).
The level of expertise and understanding among house builders and
developers varies considerably, and the stages in the process where
the need for specialist advice is likely to be required is highlighted
in the guidance.
Throughout the document, there is a strong emphasis on early and
frequent consultation with all the regulatory authorities to ensure
that a common objective is agreed, and that at every stage there
is adequate information and supporting documentation to demonstrate
the overall acceptability of the development. The importance of
consultation with the local community is stressed. This should ensure
that all information, which is relevant to the development, is available
in an open and transparent way to all interested parties, in the
spirit of the new regulatory regime, so that the disadvantages of
the present system, which often leads to blight and suspicion can
be avoided.
The recently published guidance "Communicating understanding
of contaminated land risks" from Scottish and Northern Ireland
Forum for Environmental Research (SNIFFER) is recommended to assist
in the most difficult area of public consultation and trusting relationships.11
THE WAY FORWARD
The success of the new regime will be dependent upon the regulators,
and especially the local authorities, consistently requiring a higher
standard of site assessment and risk- based management from the
developers and their consultants in the redevelopment of sites affected
by contamination, especially in the context of housing.
This will involve the application of a risk-based approach, in
accordance with guidance and best practice, to the assessment of
sites, which will inform the remediation strategy, the implementation
and post-development validation, all in an open and transparent
way, in line with the ethos of the new technical guidance and policy
approach. This will in turn increase the level of confidence which
all stakeholders can have in the redevelopment of such sites, and
avoid the potential for blight and the social and economic disadvantage
which has arisen when a robust technical approach and adequate regulatory
control has not been exercised.
The role of the environmental health officer is vital as the regulatory
officer charged with making the essential judgements concerning
the acceptability of proposed developers' remediation schemes to
adequately protect public health and the immediate environment.
It is envisaged that the new housing guidance document will provide
a valuable framework for decision-making, with the essential CLEA
publications becoming available later in the year.
The EHO's effectiveness in this field is, however, highly dependent
on the early referral of new development proposals by the planners
and developers. Recent feedback from EA-organised contaminated land
awareness raising seminars confirmed that in many authorities the
relationships between the planners and EHOs in this context was
not consistently good, and that regulatory decisions were being
left until the later stages of the planning/redevelopment process.
There is clearly a strong need for greater awareness of the important
implications of the new Part IIA regime on the processes of planning
and regeneration.
It must also be recognised that this vision can only be achieved
through effective training, for both the regulators and the private
sector, in the application and acceptance of the risk-based approach
and its many advantages to the management of contaminated land.
The EA has been responsible for the initial joint technical seminars
held throughout England in 1998/2000, and is managing the development
of a local authority Part IIA procedural guidance document which,
it is planned, will be the basis of a series of training workshops
for the local authorities in 2001.
There is clearly a need for a further extensive technical training
programme focused on risk assessment and management of land contamination,
and techniques of sustainable development. Plans need to be made
for such training to be delivered on a consistent nationwide basis
if the significant potential benefits of the new regime are to be
realised.
With reasonable progress with all these issues, it is anticipated
that the implementation of the new regime, the acceptance of the
risk based culture and the new housing guidance document, will together
play an important role in the achievement of the Government's brownfield
housing initiative objectives.
Dr Bill Baker, National Capital Projects Manager - Contaminated
Land, Environment Agency, National Groundwater and Contaminated
Land Centre, Olton Court, 10 Warwick Road, Olton, Solihull B92 7HX,
UK. Tel: 0121 7112324.
REFERENCES
1 DETR (2000) "Our towns and cities: the future", Urban
White Paper.
2 HM Treasury (2000) Spending Review 2000.
3 Syms, P, (1997) "The redevelopment of contaminated land for
housing use". A research project for the Joseph Rowntree Foundation
by the School of Urban and Regional Studies, Sheffield Hallam University.
The Incorporated Society of Valuers and Auctioneers.
4 Interdepartmental Committee on the Reclamation of Contaminated
Land (1987). "Guidance on the assessment and redevelopment
of contaminated land". ICRCL 59/83 2nd edition.
5 Government of Great Britain (1990) Environment Protection Act
1990: Part IIA, Contaminated Land, (inserted by section 57 of the
Environment Act 1995).
6 DETR (2000) DETR Circular 02/2000, " The Environmental Protection
Act 1990 - Part IIA - Contaminated Land ". The Stationery Office.
7 DETR and Environment Agency (2000), "Model procedures for
the management of contaminated land", Research Report No 11,
DETR - in press.
8 DETR and Environment Agency (2000), "The contaminated land
exposure assessment model (CLEA), technical basis and algorithms",
Contaminated Land Research Report No 10, DETR - in press.
9 DETR and Environment Agency (2000), "Guideline values for
soils", Contaminated Land Research Report, GV, DETR - in press.
10 Environment Agency and NHBC (2000), "Guidance for the safe
development of housing on land affected by contamination",
R&D Publication 66. The Stationery Office.
11 Scottish and Northern Ireland Forum for Environmental Research
(SNIFFER) "Communicating understanding of contaminated land
risks", Technical report 142.
Copies of the new "Guidance for the development of housing
on land affected by contamination" can be obtained from The
Stationery Office. Tel: 0870 6005522 or visit the web: www.thestationeryoffice.com