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without such access. Simultaneously, the instrument does not prevent it from spreading too much organic fertilizer in some
areas. A stricter manure care regulations than the current regulation with closer monitoring is considered
the most appropriate means to prevent such eutrophication.
A risk factor in this menu is that we assume that organic waste is delivered to
biogas plants. Given that the street-fee'en for waste equals combustion, composting and
Biogas treatment, there is no greater incentives for supplying organic waste to
biogas treatment versus other treatment. Given that the feed-in-tariff is set high enough, even for biogas
produced by wet organic waste, it is conceivable that this creates enough "pull" that it will be possible for
biogas plants to provide a lower gate fee than incineration and composting plants. This will
reduce the risk of a shortage of raw material is a limiting factor.
One such tool menu will help to reduce greenhouse gas emissions in the agricultural sector because it
can ensure that a portion of the potential manure is triggered by setting a sufficiently high level of support
for biogas produced in the manure. At the same time the menu to increase the use of biogas in
vehicles to air pollution especially in urban areas is reduced, and that the share of renewables in
transport increased. If 0.7 TWh of biogas is used in the transport sector can, as
described in Chapter 1, achieving renewable target in the transport sector without increasing the wagering requirement for
biodiesel and bioethanol from the current 3.5%. In addition, the menu at a good utilization of organic fertilizer, as
creating incentives for spread of suitable areas.
An alternative to the tool menu based on "pull" factors, using multiple "push" -
Factors triggering potential. A possible menu are:
Requirements for separation and biological treatment of waste and the return of nutrients to the
cycle
National target for biological treatment of organic waste
Investment of biogas plants depends on the percentage incorporation of manure in
biogas plant
Investment of gas-powered vehicles
Support for the transport of organic fertilizer for appropriate distribution areas
Such menu will cause many of the same effects as an instrument menu 1
To increase the supply of food waste from households and similar waste from any food service
and trade, it is possible to introduce legal measures leading to increased separation and subsequent
biological treatment. This requirement can be combined with a national percentage targets for the amount of
food waste to be biologically treated. This can result in a higher proportion of this waste
utilized for biogas production, while some may go to composting. Requirement
separation of food waste will not necessarily lead to a capacity-building for biogas treatment
Norway, but can lead to increased export of organic waste to Sweden and Denmark.
Investment is as previously described an efficient way of getting fired production plant
for biogas. If desired, parts of the biogas production is to use animal manure may
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to make the size of investment support for biogas plant depends on the manure-
interference ratio, see Figure 6.4 below.
Investment support for gas-powered vehicles to ensure that biogas is used in the transport sector and that
it thus leading to an improvement in air quality. Since gas engines with "lean" engine technology
For emissions that are approximately equal to diesel vehicles, investment aid should be linked to a commitment
On selecting stoichiometric engines or technology similar low emissions of NO
X
and particles.
A guide to gas-powered vehicles, however, will not be effective governance with a view to using bio gas
transport sector, but will also increase the number of vehicles that use fossil natural gas
fuel. However, this is a minor problem, when you get improved air quality regardless of
It is natural gas or biogas is used as fuel. The produced biogas is not
used in the transport sector will be used in other sectors where it will replace the same quantities
natural gas.
To ensure that the digestate spread on suitable areas can introduce a scheme which provides grants
the transport of digestate to areas that need fertilizing. In particular in animal dense areas,
which Rogaland, is eutrophication from manure already a challenge at present. With the
expected increase in livestock production, this problem could increase further. Establishment of
biogas plants that use organic waste in production (both separate treatment and
sambehandling with manure) will lead to an increase in the available amount of digestate as
fertilizer product, since waste otherwise would have been burned and thus not used as fertilizer. In areas where
there is little or no need for fertilization, the digestate having a low or negative value, and it is
appropriate from an environmental perspective transporting digestate to other areas. One can for
such as designing support scheme allowing transport of digestate outside a certain radius, will be covered
of the scheme. This will ensure that the manufacturer did not have an increased cost of transport
digestate to suitable distribution areas. The support should be linked to the quality requirements for digestate (low
content of heavy metals and other pollutants).
Figure 6.4: Proposed investment into biogas plant depends on the substrate
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Another alternative (or addition to transport support) is a support for processing of bio fertilizer. Although
fields in animal dense areas will require fertilization with nitrogen, but have little need for supply
of phosphorus. By separating bio fertilizer nitrogen in a wet and a dry fosforrik part, one could make a
nitrogen-rich product that can be spread on the ground in the area. The dry, phosphorus rich part can then
transported to areas further away where necessary for fertilization with phosphorus. In order to optimize
application of organic fertilizer can simultaneously introducing a support for analysis of organic fertilizer, as well as
Update fertilizer calculator so that it also covers different types of organic fertilizer.
An alternative to push and pull the menus is a tool menu that has as main objective to increase renewable
energy production by increasing biogas production. Given that there is a goal that biogas will
employed in a particular sector or for a specific purpose, or that the biogas should be produced by a
certain raw materials, one can introduce a simple production support in U.S. / kWh. By aligning the support
produced amount of energy given incentives to maximize gas production both through
optimization of production technology and through the choice of energy-rich feedstock. Our calculations in
Chapter 4 indicate that biogas production from organic waste is almost economically
profitable, given that waste is available and that the biogas plant is a street-fee of 700 NOK / tonne waste.
To ensure access to raw materials for biogas plant, the gate fee at the biogas plant would be less than or equal
gate-fee combustion and composting. A production support at 18 cents / kWh, according to our
calculations make it possible for the biogas plant to reduce the gate-fee'en with 200 kr / ton
waste, which could increase the supply of raw materials for biogas production. Because funding is directed to
amount of energy produced will support while providing an incentive to choose the raw material with high gas yield.
It is possible that plants may require different gate-fee for raw materials depending on the expected
gas yield, so that the supply of raw material is increased.
An alternative to a production support in NOK / kWh is a delivery support for organic waste to
biogas plant in £ / tonne. The difference in relation to a production aid is that in this case not get separated
between raw materials that provide a high gas yield and those only gives a low yield. This instrument is
therefore not as effective management with a view to getting produced with maximum energy.
As shown in Chapter 4 of biogas production based on pure manure not commercially
profitable at present (loss of around 1.27 £ / kWh). This means that a production support per
kWh will probably all the wet organic potential is triggered before any manure will be applied.
If the energy potential triggers (both manure and organic waste), the
average deficit be around 55 cents / kWh. One possibility to get triggered more of
potential than just the wet organic waste, is to provide a production support at around 55 cents / kWh,
provided that the biogas plant sambehandler manure and organic waste. In order to redeem the
potential in this way, the ratio of substrates to 4 tons manure
per 1 ton of waste.
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Review of possible new measures
The following provides an overview of new or strengthening of existing measures that will:
Increase access to raw materials for biogas plants
Increasing biogas production
Increase the use of biogas and bio fertilizer
The input to possible new measures in this chapter come from a variety of sources, such as Mepex
report (2012), Sector Report Waste Cure (TA 2592/2010; CPA 2010b), Value Chain Report for
sambehandling (TA 2704/2011) and the input that we got from the survey and the
input meeting conducted in the context of this work.
We review first instruments that can increase the supply of raw materials. Subchapter is divided into the
measures aimed at organic waste and the targeting manure. Each
These subsections are further divided into economic, legal and informational tools. Afterwards
are reviewed the various means for biogas production and use of biogas and
bio fertilizer.
To increase readability, it posted a reading guide for each instrument proposal shows
which subsection you are in:
OBJECTIVES
Instrument
Increased access
of raw material
Increased biogas
production
Increased
application
Fertilizer
Fertilizer
Wet
Wet
Biogas
Bio fertilizer
Legal
Economic
Informative
152
The review is organized as follows:
1 Measures to improve access to raw materials
1.1 Organic waste
1.1.1 Legal instruments
- Requirement for separation of food waste
- Requirements for biological treatment of waste and utilization of
nutrients in organic fertilizer
- Prohibition of incineration of waste
- Objections to the planned export of household waste and similar waste
business
1.1.2 Economic instruments
- Introduce a tax on incineration of waste if the waste is not separated
1.1.3 Informative instruments
- National target for biological treatment of waste
1.2 Fertilizer
1.2.1 Legal instruments
- Delivery obligation for manure from farms located within a certain
distance from a biogas plant
- Stricter requirements for environmentally-efficient storage and dissemination of
manure
- Incorporation Requirements manure in the feedstock for biogas plants
- Introduce emission standards for greenhouse gas emissions from manure
1.2.2 Economic instruments
- Delivery Support manure
- Support for separating manure in a wet and a dry part, if
dry part comes into biogas plant
- Reward Scheme for reducing emissions from manure
1.2.3 Informative instruments
- Information campaign on biogas production to agriculture
2 Measures to increase the production of biogas
2.1 Economic instruments
- Investment into biogas plant
- Production Support for biogas plants
- Combined investment and production support for biogas plants
- Investment support for pre-treatment of organic waste
- Innovation Support for biogas and / or pre-treatment
- Simplified application procedure for funding from Enova / Innovation Norway
3 Funding for increased use of biogas and bio fertilizer
3.1 Increased use of biogas
3.1.1 Legal instruments
- Development of standards for biogas
- Turnover Requirements for biogas in the transport sector
- Receipt Obligation for biogas in gas company
- Forced incorporation of biogas in natural gas
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- Gas Vehicles in Public Procurement
- Requirements for collection of landfill gas
- Requirements for the use of the collected landfill gas
3.1.2 Economic instruments
- Increased CO
2
Tax on fossil fuels
- Continuation of the exemption veibruksavgift for biogas and possibly natural gas
- Investment aid for the purchase of gas vehicles (private cars and / or taxi)
- Investment aid for the purchase of gas vehicles to fleet operations
- Investment aid for the purchase of gas buses
- Investment for the construction of filling stations
- Reduced disposable gas-fueled vehicles
- Support for the replacement of oil boiler to gas boiler if biogas is used
- Feed-in tariff for biogas at gas station
- Introduce a tax on natural gas unless it met a%-vis requirement
biogas intervention
3.2 Increased use of bio fertilizer
3.2.1 Legal instruments
- Stricter requirements for the storage and distribution of fertilizers
- Change the requirements of fertilizer products Regulations for heavy metal content in bio fertilizer
- Development of standards / content declaration for bio fertilizer
3.2.2 Economic instruments
- Support for the analysis of bio fertilizer
- Development of fertilizer calculator that includes bio fertilizer
- Support for the transport of organic fertilizer for appropriate distribution areas
- Support for the processing of organic fertilizer (pelleting or similar)
- Tax on nitrogen and phosphorus in fertilizers
3.2.3 Informative instruments
- Information campaign on the use of organic fertilizer
4 Transverse measures
4.1 Transverse measures to increase biogas production
- Study Support related to the optimization of environmental and climate benefits
- Improved communication between players
- National Working Group on biogas
4.2 Transverse measures to increase knowledge
- Improved statistics
- Research and development (R & D)
4.3 Transverse measures to reduce the risk of negative effects of biogas initiative
- Meta Leaks biogas plant
- Storage bio fertilizer
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M
To
L
Instrument
Increased access
of raw material
Increased biogas
production
Increased
application
Fertilizer
Fertilizer
Wet
Wet
Biogas
Bio fertilizer
Legal
Economic
Informative
1 Measures to improve access to raw materials - organic waste and
manure
1.1 Organic waste
1.1.1 Legal instruments
Requirements for separation of food waste
Description: The requirement for separation should be organized so that it entails demands for recycling, and not
Central sorting of waste, because experience shows that source-separated food waste for cleaner compost and
bio fertilizer than central sorting through the MBT method (mechanical-biological treatment) provides. If the
central sorting is used, this will reduce the value of bio fertilizer.
Many municipalities have already introduced source separation of food waste from private households. To obtain
access to food waste from the remaining municipalities and waste from the catering trade and commerce,
requirement can be introduced incrementally.
That claim is paid to food waste from households and catering industry / trade and not wet organic
waste in general, arguing that food waste from households / large households are more difficult to
get into the market without separation from other waste. Increased availability of organic waste from other types of
business (such as food processing) for biogas production, is expected to be
easier when the waste is largely generated in the clean waste streams.
The desired effect: Increase the supply of waste for biological treatment in general, and biogas treatment
particular.
Possible drawbacks: The instrument does not necessarily ensure increased access to food waste for biogas production
in Norway, as this can also lead to increased exports to biogas production in neighboring countries. It can also
lead to increased composting instead of biogas production. In addition, the requirement of an initial phase of the
the imbalance between supply and demand of food waste and available treatment capacity, but
This will stabilize over time. Instruments will likely result in increased treatment costs for
organic waste. If the instrument shall apply to all municipalities and affected industries, higher
Treatment costs can be problematic for smaller municipalities and businesses.
The implementation of this requirement will result in increased administration and supervision, as well as other
similar measures.
Conducted in neighboring countries, the Government of Sweden has adopted an interim that 50% of
food waste from households, commercial kitchens, shops and restaurants sorted out by 2018.
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