Published at : 07 Oct 2022
Volume : IJtech
Vol 13, No 4 (2022)
DOI : https://doi.org/10.14716/ijtech.v13i4.5621
Bagus Hario Setiadji | Department of Civil Engineering, Diponegoro University, Jl. Prof. Soedarto, S.H., Tembalang, Semarang, 50275, Indonesia |
M Agung Wibowo | Department of Civil Engineering, Diponegoro University, Jl. Prof. Soedarto, S.H., Tembalang, Semarang, 50275, Indonesia |
Henk M Jonkers | Department of Materials, Mechanics, Management & Design, Building 23, Stevinweg 1, 2628 CN Delf, The Netherlands |
Marc Ottele | Department of Materials, Mechanics, Management & Design, Building 23, Stevinweg 1, 2628 CN Delf, The Netherlands |
Widayat | Department of Chemical Engineering, Diponegoro University, Jl. Prof. Soedarto, S.H., Tembalang, Semarang, 50275, Indonesia |
Mochammad Qomaruddin | 1. Department of Civil Engineering, Diponegoro University, Jl. Prof. Soedarto, S.H., Tembalang, Semarang, 50275, Indonesia 2. Department of Civil Engineering, University Islamic of Nahdlatul Ulama, J |
Felix Hariyanto Sugianto | Department of Civil Engineering, Diponegoro University, Jl. Prof. Soedarto, S.H., Tembalang, Semarang, 50275, Indonesia |
Purwanto | Department of Civil Engineering, Diponegoro University, Jl. Prof. Soedarto, S.H., Tembalang, Semarang, 50275, Indonesia |
Han Ay Lie | Department of Civil Engineering, Diponegoro University, Jl. Prof. Soedarto, S.H., Tembalang, Semarang, 50275, Indonesia |
Asphalt pavement consists of
aggregates resulting in a waste material at end of its life. The aggregates can
be reused as basic material for asphalt or cementitious binding agents. In both
scenarios, the recycled aggregates should provide a good bond with the binder
to achieve strength. This study focuses on reusing recycled asphalt aggregates
(RAA) in mortar. The major weakness of RAA is the thin oily film originating
from the asphalt residue, weakening the bond with cement. The pyrolysis method
is accessed in an attempt to overcome this weakness. Three scenarios were
investigated; the use of virgin aggregates (VA), RAA, and pyrolysis recycled
asphalt aggregate (PRAA) as constituent in mortar. All
variables were set a constant except for the aggregate type, the VA mortar
function as controlling element. This research is methodologically based on
experimental data conducted in the laboratory, while aggregate samples were
taken from the field. To analyze the influence of pyrolysis to the
aggregate-to-cement bond behaviour, qualitative and quantitative data were
collected. The quantitative data were the mechanical properties, the mortar
tensile, and compression strength. The qualitative data were obtained from
scanning electron microscope readings to visually observe the aggregate surface
roughness and voids, including the aggregates cross-section and pre-existing
micro-cracks in the aggregate-to-cement interface. Supporting data were the
aggregates‘ abrasion rate
and absorption. The RAA resulted in a significant mortar strength decrease.
This conclusion was supported by the findings of pre-existing cracks in the
interfacial transition zone. The pyrolysis method improved the compression strength
but negligibly affected the tensile behavior. The compression and tensile
strength increased as a function of time for both RAA and PRAA, and a strength
convergence was reached at 28 days. The PRAA is considered an option for reuse
in mortar, supporting nature conservation.
Mechanical properties; Mortar constituent; Pyrolysis recycled asphalt aggregates
The aggregates in cementitious composites originate
from quarries or through stone crushing, which is basically recyclable (Ashadi et al., 2015; Turu’allo,
2015; Purnomo et al., 2021). Two most commonly used
recycle aggregate, i.e., recycled concrete or paving-originated aggregates,
supports the sustainability of the aggregate’s lifecycle. The main
issue when dealing with recycled aggregates is the quality: the physical
and mechanical properties that are highly influenced by the original binding
agent residue. The quality and origin of cement highly influence the alteration
of the aggregate properties when dealing with concrete and mortar. For asphalt
pavements, the asphalt is the main affecting material. The untraceable origin
and the wide range of cement and asphalts make the aggregates a very unreliable
material for recycling purposes.
The use of recycled asphalt aggregate
(RAA) in mortar has been widely studied (Abraham & Ransinchung,
2018; Sola & Ozyazgan, 2019; Debbarma et al., 2020; Shi et
al., 2020). In general, RAA from road scarifying is used directly
as a constituent in mortar. The studies concluded that the use of RAA in mortar
decreases the mechanical properties as a function of asphalt content in the
RAA. The main source of this depreciation is the poor bond. Debbarma et al. (2020) recommend
applying surface treatments (mechanically or chemically) to remove the residue
from the surface to stabilize the aggregate. The following is an overview of
methods nowadays used.
The use of microwaves for concrete
aggregate recycling started as early as 2011 and is still being investigated to
date (Akbarnezhad
et al., 2011; Choi et al., 2014; Mousa et al., 2020; Wei et al., 2021a; 2021b;
2021c). Microwave heating is also used in asphalt road
maintenance work, such as hot in-place recycling. This method does not
completely remove asphalt from the aggregate surface but only softens the
asphalt to facilitate mixing of the recycled asphalt pavement with additional
asphalt or new aggregate (Benedetto & Calvi, 2013; Sun & Sheng, 2020; Gulisano & Gallego, 2021).
Mechanically removing the thin layer of the bonding agent using acid and lime
immersion and mechanical rubbing (Kazmi et al., 2019) was also
attempted. Improving the contaminated surface was conducted by accelerated
carbonation techniques and slurry wrapping (Wang et al., 2020). The two
basic approaches differed in their method: the first was by film removal, and
the second was by treatment of the coated surface. Most recent is the
introduction of nano-silica technology through a combination of pre-spraying,
air-drying, and particle size evaluation (Gao et al., 2020; Li et al., 2021), and the
self-healing concept. The latter evolves around re-hydrating, bacterial
self-healing, and micro-encapsulation (Li et al., 2021). An
overview of methods, their advantages, and disadvantages, are outlined in the
following works (Wang
et al., 2020; Tam et al., 2021).
This work is focused on the reuse of RAA in mortar. The focus
is directed on mortar, since the behavior of mortar represents a wide range of
cement-made products such as paving blocks, concrete, and masonry. Three types
of aggregate were used: virgin aggregate (VA), recycled asphalt aggregate
(RAA), and RAA after removing the thin asphalt film using the pyrolysis method
(designated as pyrolysis recycled asphalt aggregate (PRAA)). The Pyrolysis
method is a unique new surface treatment method to remove and stabilize the
residual asphalt film by heating and is expected to contribute to increasing
the mechanical properties of the mortar due to an aggregate-to-mortar bond
improvement.
Research on pyrolysis of recycled asphalt aggregates is limited.
Most of the work on improving recycled aggregates does not focus on pyrolysis
to stabilize the residual film surrounding the aggregates. Comparing the impact
of methods in general, recycled aggregates result in a decrease in compressive
and tensile strengths due to the residue of previous binding agents and the
non-standard quality of the original material, as stated in the majority of
previous research works. The attempt to remove the residual film using a broad
range of methods showed that the mechanical properties of the new composite
using mortar or asphalt as the binder improved, but could never reach the
strength of the original virgin aggregates (VA).
The findings in this study showed that, in compression, the
decrease was independent of mortar age; the strength reduction was 55% and 30%
for the RAA and PRAA mortars. The strength loss of the RAA predominantly
originated from the surface conditions: the thickness of asphalt film, smoother
surface, pre-existing micro-cracks, which promote crack initiation and
propagation under loading, and the decrease in abrasion resistance, in
combination with the presence of loose, unstable particles. The PRAA had a
better compression strength, but, despite the removal of the asphalt film, a
thin layer of residue remained. The PRAA had a relatively high abrasion rate,
weakening the bond between the aggregate and the cement. While no preliminary
micro-cracks were present in the aggregate surface and the absorption rate was
better compared to RAA, substantial pre-existing cracks were detected in the
aggregate-to-mortar interface.
In tension, both the RAA and PRAA exhibited a 40% strength
decrease, which is slightly fluctuates with age and stabilises at 28 days. The
pyrolysis did not substantially affect the tensile behavior due to the presence
of pre-existing cracks. The relationship between the tensile and compression
strength can be represented by the coefficient C ranging from 1.3 and 1.2 for the VA and RAA, and 1.0 for the
PRAA, using the equation at any age from 14 to 180 days.
The RAA had a 1.49% absorption, but the PRAA had a substantially
lower absorption of 0.59%. The pyrolysis stabilized the surface and prevented
water intrusion into the aggregate's inner pores.
The pyrolysis method applied on RAA had a number of advantages:
the compression strength increased, and the absorption decreased, reducing the
formation of a water film surrounding the aggregate during the cement hydration
process. The pyrolysis procedure did not have any impact on the tensile
strength for both the RAA and PRAA, however, the overall tensile strength
decrease was relatively low, with a minimum reduction of 42% in the VA mortar.
The pyrolysis procedure offers a solution to rejuvenate the RAA for mortar
usage. The reuse of RAA supports the conservation of natural aggregates.
This
research was financially supported by the Faculty of Engineering, Diponegoro
University, Indonesia through the Excellent Research Grant 2021 [grant number
3179/U/1/UN7.5.3.2/PP/2021].
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