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3.2 Best Practicable Environmental Option (BPEO) for
Municipal Solid Waste (MSW)
The following paragraphs describe in detail the BPEO for
the management of municipal solid waste in the North East. This is shown
graphically by Table 3.3 and the estimated tonnages of waste managed
by the various components of the BPEO are shown in Tables 3.4 to 3.7.
In developing the North East AWP, the Waste Strategy Area
Group was concerned to ensure an open and transparent process and one,
which would encourage stakeholder involvement. The North East Area Waste
Plan has therefore developed through close partnership working between
Aberdeenshire Council, Aberdeen City Council, Moray Council, Scottish
Environment Protection Agency, Scottish Enterprise Grampian and Scottish
Enterprise Moray Badenoch and Strathspey, as well as the voluntary sector,
the waste industry and waste producers. It also took into consideration
the findings from the public consultation held throughout July and August
2002.
The BPEO for the management of MSW in the North East is
summarised in Figure 3.2.
Figure 3.1 - North East MSW Best Practical Environmental
Option

The BPEO sets strategic targets for the Waste
Strategy Area, detailed in this section. Local authority waste implementation
plans will devise the localised delivery systems based on each of the
local authoritys ability to achieve a proportion of the BPEO for
the North East.
3.2.1 Waste Prevention
In working with the National Resource and Waste
Forum (NRWF), SEPA is developing a national framework to guide the work
of the waste strategy groups and other key players on waste prevention.
This will include research into best practice, both within the UK and
abroad. The outputs from this research will be twofold:
- Practical guidance to Waste Strategy Area Groups
on how to develop their own local waste prevention plan, and the various
tools and techniques to choose from.
- National recommendations to policy makers and
others on instruments that have been demonstrated as successful in
preventing waste.
The North East Waste Strategy Area Group will then draw
together a local stakeholder group with the remit to identify existing
waste-prevention initiatives and develop a North East area waste-prevention
plan. This plan will set targets, identify actions to be undertaken
locally and will tie in to national initiatives on education, promotion
and emerging policy instruments.
3.2.2 Reuse and Refurbishment
The reuse and refurbishment of waste is implicit in the
North East AWP. Value is retained and the reuse and refurbishment activities
can be used to stimulate social inclusion by providing employment and
producing goods, which can be used by those who would otherwise struggle
to afford goods of that type. The not-for-profit sector have an important
role in taking this forward, for further details of local initiatives
see Text box 2.
Action 13
Work with national awareness raising bodies (e.g. SWAG, RAGS) and
local organisations (e.g. NESBWMP) to help develop and realise the objectives
and targets of the AWP.
3.2.3 Recycling
The BPEO requires a significant increase in the
quantities of materials collected and forwarded to reprocessors for
recycling. This will involve significantly increasing the segregated
kerbside collections of paper, plastic, textiles, and ferrous and non-ferrous
metals. It is possible that glass will also be collected in this way,
however, any collection system which produces a mixed (colour) glass
fraction will limit the reprocessing options for glass. To achieve the
recycling targets set out in Table 3.1, an increase in household participation
in segregated kerbside collections will be required to beat least 86%.
This is illustrated in Figure 3.2, which shows indicative levels of
participation in segregated kerbside collection of recyclables which
requires to be achieved in each of the target years.
Aberdeenshire and Moray Council intend to reduce
the capacity of the residual waste collection and make a kerbside recycling
service available to 86% of households, with the balance being covered
by an enhancement to the councils recycling centres.
Aberdeen City Council intends to reduce the volume
of residual waste by introducing a segregated kerbside collection for
dry recyclables to 100% of households, with the balance being served
by the conversion of 1 in 4 communal street bins to recycling bins.
Table 3.1 - Levels of Kerbside Segregated Collections
of Dry Recyclate
|
% Of Households served |
| Year |
Aberdeenshire Council |
Aberdeen City Council |
Moray Council |
| 2006 |
86% |
86% |
86% |
| 201020 |
86% |
100% |
86% |
There are a number of methods by which segregated kerbside
collection can be undertaken. The method chosen will be dependant upon
housing type and geographical location and will be determined after
further investigation.
In addition to segregated kerbside collections, there
will be a need to progressively increase the number of mini recycling
centres in each of the three local authority areas. These bring-to
sites will cater for households who do not have segregated kerbside
collections. Table 3.2 gives indicative numbers of mini recycling centres,
which will be established in each of the local authority areas. The
actual numbers required will be dependant upon the extent and success
of segregated kerbside collection schemes and local housing density.
In addition, new facilities and infrastructure will be
required in order to sort and package recyclable materials prior to
onward transportation to reprocessors. This may involve an upgrade of
existing transfer stations or alternatively the provision of a dedicated
MRF.
Table 3.2 - Number of Additional Mini Recycling Points
Required
|
Number of Additional
Mini Recycling Centres (1) |
| Year |
Aberdeenshire Council |
Aberdeen City Council |
Moray Council |
| 2010 |
42 |
15 |
57 |
(1) Total planned
Aberdeen City Council will be converting 1 in 4 street
bins in the city centre to collect dry recyclate resulting in a total
of 936 recycling bins. The communal recycling bins will be used by the
surrounding households but can also be used by members of the public.
3.2.4 Composting
Increasing the quantity of separately collected compostable
kitchen and garden wastes will also be required. This will be achieved
through the introduction of segregated kerbside collections (kitchen
and garden compostables) and enhancement of recycling/civic amenity
sites (provided with separate skips for compostable garden wastes).
To achieve the composting targets will again require increasing householder
participation rates in segregated collections. This is illustrated in
Table 3.3, which shows indicative levels of participation in segregated
kerbside collection of compostable wastes that require to be achieved
in each of the target years.
In partnership with the Recycling Advisory Group Scotland
(RAGS), Aberdeenshire Council has appointed a community liaison officer
to build on the success of previous home composting initiatives and
work directly with communities. The liaison officer will work to develop
the community-recycling network, with an emphasis on community composting
schemes. In terms of centralised composting, as Aberdeenshire Council
currently applies a composting process to treat mixed waste, it has
no plans to introduce a segregated green waste collection. The mixed
waste will be subject to source segregation, following the introduction
of kerbside collections of dry recyclates. However, the council retains
the capacity to introduce a more intense source segregated collection,
should it be required by future legislation.
Action 14
Identify and encourage communities to participate in home composting
schemes.
Table 3.3 - Number of Households Participating in Segregated
Kerbside Collections of Compostable Wastes
| Year |
Number of Households
Participating |
Area Total |
| 2006 |
23,318 Moray
45,000 Aberdeen City |
68,318 |
| 2010-20 |
23,318 Moray
60,000 Aberdeen City |
83,318 |
Aberdeen City Council launched a segregated kerbside green
waste pilot in April 2002 and this will be extended to all households
with gardens by 2010.
Moray: The current on farm composting of garden
waste will be extended when the kerbside collection of green waste commences.
The council will continue to collect and shred this waste prior to handing
over to a local farmers for composting.
An in-vessel composting plant will treat the segregated
waste fines from the existing treatment plant at Moycroft, Elgin. Trials
are being undertaken in conjunction with Aberdeenshire Council on the
use of their in-vessel plant.
3.2.5 Other Recovery
The BPEO recognises the need for an element of thermal
treatment as one of the waste treatment options to ensure the BMW targets
for 2010 and subsequent targets are met.
However, due to the potentially long lead time for the
development of an energy from waste plant (in terms of planning and
permitting), action should be taken as early as possible to ensure that
facilities are in place to meet the targets set by the Landfill Directive.
However, it is clearly unacceptable to move from a regime
of landfilling to one that advocates total thermal treatment in any
of its forms. There are fractions of the waste stream that are non-renewable
resources, such as plastics and, arguably, some of the paper waste.
Aluminium and ferrous wastes will not enhance the thermal performance
of a plant and will be recovered prior to processing. Any thermal treatment
for recovering the energy value of the waste will be for that fraction
of the waste that is not practical for recycling. Ensuring that only
those wastes, which are best suited for combustion, are combusted and
those suitable for recycling are recycled. SEPAs emerging policy
on the use of energy recovery technologies supports this strategy.
3.2.6 Disposal to Landfill
MSW that is not recycled, composted or treated in the
energy from waste plant will be disposed of to landfill. In addition,
reject material from all these processes will also be landfilled.
Aberdeen City has no landfills licensed to take MSW. Waste
at present is handled by SITA and disposed of in Aberdeenshire or exported
to Bin landfill near Perth. Aberdeenshire Council use their own landfill
sites at Banchory and Brandon Howe and private sector landfills at Stoneyhill
and Wester Hatton. Wester Hatton site has been provisionally classified
as a hazardous landfill so may not be able to accept MSW in the future.
Stoneyhill landfill has a provisional closing date of 2008 and as they
will be accepting waste from Highland Council, its lifetime must be
regarded as significantly shorter than 5 years. Brandon Howe is expected
to close in 2006, leaving only the Banchory site with significant licensed
capacity post 2008. As a result, landfill capacity in the North east
is being reviewed. Moray Council has capacity until end of 2021.
3.2.7 Household Hazardous Wastes
Household hazardous wastes such as batteries, pesticides,
solvents, etc., contain chemicals that are potentially toxic. If these
wastes are not removed from the waste stream they can adversely affect
the environmental performance of the waste-management techniques employed
to manage MSW. Collections of these materials will be reviewed by the
Waste Strategy Area group.
A national partnership project is being delivered to investigate
the options available to Local Authorities in Scotland for collecting
household hazardous waste separately from the domestic waste stream.
Once an initial study has taken place to review the current situation
on household hazardous waste recovery in the UK and Europe, and what
future legislation will mean for local authorities, pilot collection
trials will be implemented to accurately determine the logistical and
economic realities of separate household hazardous waste collections.
The project will also investigate current public awareness of the issues
to develop effective education campaigns.
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