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4. Managing Non-Municipal Solid Wastes
4.1 Non-Municipal Solid Wastes National Framework
Over 12 million tonnes (1)
of waste arose from Scotlands homes, shops, offices and industry
in 1998. Currently, however, due to the lack of complete and robust
data for all wastes, the development of the Best Practicable Environmental
Option (BPEO) for the Lothian and Borders has initially focused on just
2.9 million tonnes of this total waste stream produced in Scotland
municipal solid waste (MSW), e.g. household waste and any other
waste under the control of local authorities or their agents acting
on their behalf (The Landfill Directive: A Consultation Paper, 17 November
1999, Scottish Executive).
This chapter focuses on non-Municipal Solid Wastes (non-MSW).
These consist of all industrial wastes, all commercial wastes not collected
by the Local Authorities, non-natural agricultural wastes, and mines
and quarries wastes.
A framework to address the management of non-MSW wastes,
which forms the largest part of the wastes produced in Scotland, has
been developed through a partnership between representatives from the
following organisations SEPA, Scottish Executive, the Enterprise community
and the waste management industry. These wastes will be a major focus
for the future development of the National Waste Strategy: Scotland
and local Area Waste Plan.
Non-MSW is more complex than Municipal Wastes collected
by the Local Authorities, and significant data gaps exist. Whilst the
BPEO process initially developed by SEPA has been successfully applied
to MSW, it has become apparent that the process needed to be reviewed
and redefined when dealing with other waste streams.
Continuing the partnership approach that is at the heart
of the NWSS development, a multi-stakeholder group was brought together
to obtain preliminary views and input into a management approach for
non-MSW.
The key issues for non-MSW are:
1. Waste Arisings Data
the lack of requirement to record and report waste arisings data
has contributed to the absence of sufficiently detailed data required
to make a BPEO decision.
2. Producer Behaviour
tools that are currently available and those that need to be
developed further to influence the behaviour of commercial and industrial
waste producers to ensure the adoption of the BPEO.
3. Non-Municipal Solid Wastes
Plan provision of a detailed plan to ensure that the
NWSS and local Area Waste Plans (AWP) deal with all controlled wastes
and not just focus on MSW.
4.1.1 Specific Waste Streams
Using the Consolidated European Waste Catalogue (August
2002) all listed wastes have been grouped into compatible industry sectors
and will form the basis of future work for non-MSW. These groupings
also include agricultural, mining and quarry wastes that are currently
not controlled wastes but will imminently be included with the controlled
waste-regulatory regime.
Any links with the current Priority Waste Stream programme
and existing Technical Guidance, Best Practice, etc., have been made
along with possible links to current BPEO technology options for MSW
as set out in section 3 of the Area Waste Plan.
The waste groupings are detailed in Table 17 following:
Table 17 - Waste Groupings
| |
Waste Grouping |
| A |
Exploration, mining, quarrying and physical/chemical
treatment of minerals |
| B |
Animal/fish wastes (agriculture, aquaculture,
hunting, fishing, food preparation/processing) |
| C |
Plant wastes (Agriculture, Aquaculture,
Forestry, Food Preparation/Processing, Paper and Wood Industries) |
| D |
Leather, fur and textile Industries |
| E |
Petroleum refining, natural gas purification
and coal pyrolysis |
| F |
Wastes from inorganic chemical processes |
| G |
Wastes from organic chemical processes |
| H |
Wastes from thermal processes |
| I |
Wastes from surface treatments/coatings
(metals and other materials) |
| J |
Waste organic solvents, refrigerants
and propellants |
| K |
Waste packaging (including absorbents,
wiping cloths, filter materials and protective clothing) |
| L |
Wastes not Otherwise Specified (Tyres,
Batteries, Vehicles and Electrical/Electronics Wastes) |
| M |
Construction and demolition wastes (including
soil from contaminated sites) |
| N |
Human and animal healthcare wastes (including
research wastes/excluding kitchen wastes) |
| O |
Water industry wastes (incl. water/sewage
treatment wastes) |
| P |
Other waste industry wastes |
4.1.2 Project Timetable
A list of criteria have been developed to classify the
wastes into high, medium and low priority projects. These have been
based on the following considerations
- Links to Municipal Solid Waste BPEO
- Sectoral Importance (to the Scottish Economy)
- Infrastructure Shortfall in Scotland
A further prioritisation stage has also taken place on
the current and future regulatory/legislative requirements for the wastes
to be addressed.
These projects will be managed at either the local or
the national level depending on the geographical distribution of arisings.
Section 4.2 details how this Area Waste Plan will contribute to the
outputs of these projects.
See national plan for further detail on the identified
non-MSW projects.
4.1.3 Project Groups and Outputs
Technical groups will be established consisting of the
key waste producers and managers of the waste groupings (Table 17) to
drive the range of projects forward. The membership of these groups
is very important to ensure ownership and acceptability of the project
outputs by those sectors that produce and manage these wastes for the
future. The groups will undertake and commission work that will seek
to provide the following recommended outputs:
- Establish reliable baseline data and existing
regulatory controls
- Report on current practices to deal with waste
- List current facilities and technologies
- Identify emerging technologies and processes
- Recommend good practice and links to existing
best practice guidance
- Provide guidance on identifying local BPEO and
the use of Life-Cycle Assessment
- Identify problematic wastes that may require
further research
- Identify waste minimisation tools
- Identify skills gaps and training opportunities
- Identify barriers to achieving BPEO and recommendations
to overcome
- Describe benefits and opportunities to implementing
BPEO
- Identify necessary regulatory controls and other
drivers
- Identify any necessary economic and regulatory
impact assessments for the sector
- Identify enterprise opportunities and social
benefits.
4.1.4 Self-Assessment Guidance for BPEO Decision Making
Whilst it is recognised that not all wastes can be addressed
as a high priority and the timetabling of BPEO projects will be over
the longer term, there are opportunities to encourage the widespread
use of the BPEO decision-making processes that consider environmental,
economic and social aspects when dealing with these wastes. The development
of generic Self-Assessment BPEO Guidance for Industry will provide a
valuable and consistent process for waste producers, waste industry
and waste regulators alike, when making localised assessments on the
best sustainable options available and the use of life-cycle assessment.
In order to achieve widespread industry ownership and credibility of
the guidance, it shall be developed in an inclusive manner with consultation
involving key stakeholders and will be undertaken on a national level.
Notes
(1) This figure does not include agricultural, mining and quarrying
wastes as these are currently not controlled wastes as defined by the
Environmental Protection Act 1990.
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