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5. RDF/SRF QUALITY MANAGEMENT INITIATIVES

5.4. SRF product quality standards for specific end-uses

5.4.1. Specifications for end uses vs. classification

2002

Class codes are a tool for identifying and pre-selecting SRF by giving an immediate, but

2003

inevitably simplifying, image of the SRF quality. However, class codes cannot predict the

2004

actual performance of SRF when used (see TABLE 2) for a list of possible RDF/SRF uses).

2005

Definition of specific SRF properties and value ranges, thresholds and limits most relevant to

2006

each SRF utilisation plant in accordance with the particular technical characteristics, and

2007

legal demands of each thermal recovery process, is imperative for its marketability36.

2008

In order to appropriately characterise SRF, physical-mechanical, chemical and biological

2009

descriptors should be identified. Ultimate and proximate analyses are the minimum

2010

prerequisite to assess the thermal recovery behaviour and performance of a fuel197.

2011

Specifying SRF according to the CEN guidance demands a general list of obligatory and

2012

voluntary descriptors to be quantified. Properties should be measured according to

2013

appropriate, existing, or under development, CEN standard methods190. However,

Thomé-2014

Kozmiensky133and Beckmann et al.36stressed that effective use in varying applications

2015

demands the determination of a more complete list of properties (TABLE 14).

2016

2017

<<Table 14>>

2018

2019

For example, characterisation of the reaction-related properties is critical, especially for

2020

co-combustion applications. For instance, Hilber et al.198have recently developed a method

2021

for assessing the process-specific combustion behaviour of low in char-formation RDF/SRF:

2022

the de-volatilisation of SRF at specific temperatures is measured by multi-sample

thermo-2023

gravimetric analysis (TGA). In the case of biofuel QA/QC, which has similarities with

2024

WDFs, the significance and interrelationships of important physical-mechanical fuel

2025

properties have been investigated by Hartmann199; and the chemical properties reviewed by

2026

Obernberger et al.200. Eckardt and Albers46investigated the current use of specification

2027

properties and limits proposed by plant operators in various thermal recovery applications of

2028

SRF.

2029

However, even within each specific category of RDF/SRF end-uses, it can be

2030

challenging to agree upon defensible specifications that are applicable to every end-use. A

2031

wealth of available expertise has been incorporated in the relevant CEN report196. Despite

2032

that it might still be evident that there is limited understanding of RDF/SRF behaviour within

2033

the various possible thermal recovery systems, resulting in the absence of robust technical

2034

and environmental criteria for their use as substitute fuel46. Furthermore, generalisation on

2035

fuel combustion behaviour is not advisable, and plant-specific investigations are preferable,

2036

because, for instance, transfer factors for elements of concern are highly process and

2037

operation mode-specific36, 196, 198

. In addition, it is usual practice for each plant to prepare its

2038

own unique blend of substitute and raw fuels, leading to varying, case-specific contract

2039

specifications5, 46.

2040

In co-combustion of RDF/SRF with fossil fuels (and other WDFs), the actual degree

2041

of substitution varies, depending on the comparable quality of the RDF/SRF with the rest of

2042

the fuels, along with any related legal stipulations. Substitution of the original fuels by

2043

RDF/SRF depends on compatibility of the RDF/SRF properties with the thermal recovery

2044

process, typically designed for fossil fuels. For example, pulverised hard coal-fired plants

2045

with wet bottom boiler types (i.e., with molten slag with cyclones) (WBB) are more tolerant

2046

to the shape and dimensions of SRF, in comparison to plants with dry bottom boilers

2047

(DBB)196. It has been estimated that coal-fired plants may reach up to 20%w/w. substitution

2048

in the long run190; for cement kilns the percentage may vary between 50-100%w/w.

2049

Dedicated fluidised bed combustion (FBC) and gasification/pyrolysis plants are not

2050

constrained by such limitations. However, Beckmann and Thomé-Kozmiensky45stressed

2051

that substitution rates as low as 1%w/w. have been established for various thermal SRF

2052

recovery applications in the German state of North Rhine Westphalia. Even these low

2053

substitution rates have to be proven in future practice and for higher rates process-specific

2054

limit values should be convincingly defined for reaction kinetic properties. For

2055

confidentiality reasons, contract-based specifications do not often fully reach the public

2056

domain. This constrains the development of a wider consensus on what constitutes accepted,

2057

fit-for-purpose RDF/SRF quality.

2058

Nevertheless, it has been argued that maximum acceptable concentrations of trace

2059

elements of concern in SRF may be used to indicate its environmental suitability for a certain

2060

end-user190. Maximum values exist in national legislation regarding blending of wastes with

2061

fossil fuels. They usually apply to the most volatile elements, namely Hg and Cd or Cd+Tl.

2062

Standards also apply to the “sum of other heavy metals.”33. An indicative list of SRF

2063

environmental classes that could be accepted for certain technologies, based on conservative

2064

assumptions for trace elements is presented in TABLE 15.

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<<Table 15>>

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van Tubergen et al.190calculated estimations for the value ranges of SRF class-coding

2069

properties that could be accepted for different end-uses. For comparison, Eckardt and

2070

Albers46provided data on Cd, Hg and Tl limits specified for SRF by certain thermal recovery

2071

commercial references in Germany.

2072

The most important descriptors and acceptance values/classes for the main SRF

end-2073

users, focusing on potential properties of concern, are discussed below. Beckmann and

2074

Thomé-Kozmiensky36have detailed the experience in Germany. SRF particle form, size and

2075

shape exemplify the differences in the end-user specifications and NVC are discussed

2076

separately.

2077