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In document Atención religiosa al final de la vida (página 65-77)

Task 2 commences with the identification of WtE techniques. The three-step data collection strategy used for this task is illustrated in the figure below.

In Task 1, the main waste treatment pathways were defined and arranged into five groups as follows:

Group WtE pathway

Group 1  Combustion plants: Combustion plants which utilise waste as a secondary energy source in combination with other types of fuels (these installations include all kinds of conventional power plants used for the generation of mechanical and/or electrical power generation and heat, as well as recovery boilers)

Group 2  WI plants: Waste incineration plants dedicated to the thermal treatment of waste, with recovery of the combustion heat, through the direct incineration by oxidation of waste

Group 3  CL plants: Cement and lime production plants Group 4 AD plants: Anaerobic digestion plants

Group 5 Other WtE plants: Other waste-to-energy plants (including pyrolysis, gasification, plasma treatment and hazardous waste incineration) Within each group, the techniques are split into two subgroups: the first subgroup lists techniques which are considered to be proven techniques that could be implemented immediately in any Member State to improve the deployment of WtE with respect to energy recovery. They will have a Technology Readiness Level (TRL) of at least 9 (for further discussion of TRL, please refer to Section 4.2.2 below).

The second subgroup lists emerging WtE techniques which are considered ‘Technologies to watch’. These technologies all have a TRL level of 8 or less. This TRL level indicates that they are currently not commercially mature but may offer potential in the future. An evaluation of all techniques was performed according to the methodology described below in Section 4.2.

4.1.1 Summary of WtE pathways

A high-level summary of the advantages and disadvantages of each of the five WtE pathways is provided below.

Advantages Disadvantages

Combustion plants

co-incinerating waste  Existing combustion plants may be able to be modified, avoiding

extensive new build

 The efficiency of electrical energy recovery can be high due to high boiler operating temperatures and pressures

 Requires the whole combustion plant to be permitted by the relevant national environmental agency and to be compliant with the IED

 The percentage of waste by weight that can be co- incinerated with most non- waste feedstock is small in many cases (often around 5%)

Waste incineration plants

 Proven and bankable technology which tolerates a wide range of wastes

 Ideal for district heat and cooling connections to increase overall plant energy efficiency

 Electrical energy recovery efficiency in a steam boiler is limited due to the

corrosive nature of waste feedstock

 The siting of waste incinerators can be

controversial due to public perception

Cement and lime (CL) plants

 Some of the waste material content is recycled into the cement clinker

 The thermal conversion process will always recover a high proportion of the waste input energy content regardless of plant location

 CL plants require a highly processed waste-derived fuel (SRF) with exacting quality standards which requires energy to produce

 The demand for cement is variable meaning that CL plants demand less waste feedstock during periods of low economic activity

 CL plants can have higher emissions compared to WI plants

Anaerobic digestion

(AD) plants  AD plants are relatively uncontroversial due to low or negligible emissions

 AD plants produce a digestate by-product which can be spread on land under most

circumstances

 Energy recovery through a gas engine gives low overall electrical efficiency

 Collecting large quantities of suitable uncontaminated organic feedstock can be challenging

products (such as

polymers) rather than just heat and power

 Although not an advantage of the

technology itself, due to the innovative nature of some other WtE

processes, financial support through grants or incentives may be

available in some Member States

transition from

demonstration scale to commercial reality

 Some waste streams suitable for other WtE processes are limited in size and availability

The energy efficiency of each pathway is also summarised below for both current average (Av) and optimised (Opt) net annual average energy efficiency. Average net annual average energy efficiency represents the current situation, optimised net annual average energy efficiency represents the efficiency WtE could reasonably achieve if improvement techniques are implemented. The methodology which has been used to calculate these efficiencies is explained in full within Section 4.2.

Energy recovered as electricity, efficiency 1 Energy recovered as heat, efficiency 2 CHP

recovery efficiency 3 recovery Energy to fuel, efficiency Av

% Opt % Av % Opt % Av % Opt % Av % Opt % Electric Heat Electric Heat

Combustion plants 4 36 40 - - - - WI plants 22 5 33 6 72 7 80 8 17 9 51 9 27 10 66 10 - - Total 68 Total 93 CL plants 11 - - 75 80 - - - - - - AD plants 18 12 23 13 - - 18 14 18 14 - - - 41 15 Total 36 Others 20 16 35 17 75 16 80 8 - - - - - 40 18

Net annual average efficiency:

1 100% electrical load. 2 100% heat load.

3 CHP - 80% of heat sold annually, 100% electrical load.

References:

4 LCP BREF, coal / lignite pulverised combustion.

5 ISWA CE report 2015, gross existing plant efficiency corrected to net efficiency.

6 AEB Amsterdam / Martin GmBH statistics, refer also High Steam Parameters for Boilers and

Superheaters proven technique.

7 CEWEP.

8 Ricardo estimate based on known boiler efficiencies.

9 Annual average efficiency based ISWA CE report 2015 existing CHP plant gross efficiencies, corrected to

10 Annual average efficiency based on optimised AEB / Martin GmBH net electrical efficiency and ISWA CE

report 2015 high efficiency CHP plant gross efficiencies, corrected to net efficiency with annual average heat load.

11 CEMBUREAU.

12 ISWA CE report 2015, AD plant net efficiency.

13 UK Department of Energy and Climate Change, Advanced AD net efficiency. 14 ISWA CE report 2015, net efficiency with annual average heat load.

15 ISWA CE report 2015, net efficiency of biomethane production at 100% annual load. 16 Typical net power / heat only efficiency of a gasification system as an emerging technique.

17 High efficiency claimed by optimised emerging techniques suchas Two Stage Combustion with Plasma

with energy recovery through an internal combustion engine.

18 Typical net efficiency of an emerging technique producing a fuel product.

In document Atención religiosa al final de la vida (página 65-77)