Published at : 24 Dec 2024
Volume : IJtech
Vol 15, No 6 (2024)
DOI : https://doi.org/10.14716/ijtech.v15i6.7328
Dalhar Susanto | Research Cluster of Architectural Science and Building Technology (ASBT), Department of Architecture, Faculty of Engineering, Universitas Indonesia, Jl. Prof. DR. Ir R Roosseno, Depok 16424, Indonesi |
Rasha Hanuna Shahab | Research Cluster of Architectural Science and Building Technology (ASBT), Department of Architecture, Faculty of Engineering, Universitas Indonesia, Jl. Prof. DR. Ir R Roosseno, Depok 16424, Indonesi |
Miktha Farid Alkadri | Research Cluster of Architectural Science and Building Technology (ASBT), Department of Architecture, Faculty of Engineering, Universitas Indonesia, Jl. Prof. DR. Ir R Roosseno, Depok 16424, Indonesi |
Safi Brahim | Research Unit: Materials, Processes and Evnironment, Faculty of Technology, M’hamed Bougara University of Boumerdes, Frants fanon city, 35000 Boumerdes, Algeria |
Earthquake activity in Indonesia increases annually, causing more victims to require shelter and a rise in disaster waste. This waste can pose health risks and safety threats to humans, making careful management essential. One way to address this issue is recycling or reusing disaster waste materials to construct shelter. Therefore, this study aimed to investigate the performance of earthquake waste materials, recycled or reused as post-disaster shelter. To achieve this objective, a case study was conducted in Cianjur, Indonesia, where a recent earthquake occurred, and waste material samples (red brick, ceramic tile and roof tile) were collected for testing. Moreover, the compressive strength of the materials was measured in comparison with new building materials. The results shows that ceramic tile and roof tiles meet the compressive strength standards and can be reuse for post-disaster shelters, with compressive strengths of 17.7 MPa and 21.8 MPa.
Compressive strength; Disaster waste material; Post-Disaster shelter
1.1.
General Background
Indonesia is situated along the Asia-Pacific Ring of Fire, a region characterized by frequent volcanic and seismic activity (BNPB, 2023). This "active zone" experiences numerous earthquakes annually, with 22 out of 10,792 major earthquakes recorded in 2022 (Dandy, 2023). Increased earthquake activity can lead to greater damage, displacing victims whose homes are destroyed and requiring safe shelter. In 2023, approximately 104.226 disaster victims required shelter (BPS, 2024). Effective shelter should provide security, comfort, protection, clean water, and proximity to essential facilities (UN/OCHA, 2008). In addition to causing displacement, earthquakes generate significant amounts of waste. For example, Lombok earthquake produced an estimated 15-20 kg of waste per day (Wibowo and Anugrah, 2017), and the 2021 East Flores in East Nusa Tenggara earthquake left 2,587 out of 85,755 houses heavily damaged (BNPB, 2021). Accumulated disaster waste poses health risks, and hazardous materials can increase safety threats, necessitating proper waste management. Recycling or reusing disaster waste materials to construct shelter is one viable solution to mitigate these challenges (UNEP, 2008).
1.2.
Related Studies
The United Nations Environment Programme (UNEP, 2008) defines disaster waste as accumulated
construction debris and sediment from landslides caused by seismic activity.
This waste poses health hazards due to the presence of chemical and biological
contaminants, necessitating effective waste management. Managing natural
disaster requires the implementation of effective policy, timely response, and
appropriate preparedness measures (Berawi, 2018).
Earthquake waste management practices vary across countries, but the Joint
UNEP/OCHA Environment Unit outlines a guideline with three stages, namely
emergency, early recovery, recovery, and contingency planning (MSB and JEU, 2011). According to (UNEP, 2008), in Indonesia, there are two stages
in managing earthquake waste materials, namely pre-disaster and post-disaster.
Pre-disaster focuses on mitigation measures, such as securing land leases or
permits and developing programs to handle building debris effectively during
emergencies. Meanwhile, post-disaster addresses recovery or reconstruction. It
includes identifying waste at the disaster site, assessing its characteristics
and capacity, evaluating risks, and determining priorities. Separating waste
materials can increase the percentage of recyclable materials and raise public
awareness (Kristanto, Gusniani, and Ratna, 2015).
Disaster waste materials are categorized into plant debris, soil and sediment,
domestic waste, and construction materials, such as bricks, wood, and concrete.
Construction materials can be recycled or reused as aggregates or building
materials for constructing shelter.
Shelter is essential for improving health, supporting
families, ensuring security, providing protection from weather, and saving
lives during crisis or post-disaster recovery (Sphere
Association, 2018). Furthermore, it is defined as a place that offers
comfort, access to clean water, and proximity to essential facilities including
workplaces, educational institutions, and healthcare centers (UN/OCHA, 2008). Shelter can also be understood as
a space equipped for human habitation (Sinclair,
2006). According to (Krimgold, Davis, and
Thompson, 2015), and (IFRC, 2013), (Sinclair,
2006), post-disaster shelter includes transitional stages before victims
move to permanent housing. These stages include emergency,
temporary/transitional, and progressive/core shelter. Emergency shelter is a
short-term solution that provides basic support immediately after a disaster.
It is constructed using materials that can be quickly dismantled and
reassembled, such as plastic sheets with wooden poles and ropes.
Progressive/core shelter is designed with materials that allow for
transformation into permanent housing. It typically includes one or two rooms
and may also serve as transitional shelter when recovery efforts take longer.
According to (PMI, 2019), (Krimgold, Davis, and Thompson, 2015), and (Wilson, 2011), several criteria should be considered when
reusing and recycling disaster waste materials for shelter, including security,
comfort, long-term planning, and adherence to basic construction standards.
Ensuring the quality of materials is crucial for constructing a shelter that is
durable, environmentally friendly, affordable, and accepted by the local
community. These objectives can be achieved by using high-quality materials,
maintaining proper construction practices, and engaging experts and local
communities. Shelter construction criteria are particularly relevant to this
study, with a specific focus on the reuse and recycling of disaster waste.
Furthermore, the strength of waste materials is a key consideration,
specifically in disaster-prone areas where safety and durability are paramount.
Several studies have investigated the reuse and recycling
of disaster waste materials. For instance, (Al-Zaid,
2020), (Parura and Rahardyan, 2020),
and (Sunoko, Prijotomo, and Noerwasito, 2016)
examined disaster waste management techniques, structural methods, straw
systems, beam systems, and manufacturing processes. Although these studies
offered practical solutions for post-disaster shelter construction, there is no
extensive testing of material properties to ensure quality. (Pradani et al., 2023) also investigated
the recycling of disaster waste into flexible pavement materials such as
aggregates, asphalt, and bitumen. Therefore, this current study aimed to
evaluate the reuse and recycling of disaster waste materials through a case
study in Cianjur, Indonesia, and material strength tests. Strength is defined
as the maximum stress a material can withstand under an external force (load)
without failure (Zhang, 2011). Strong materials resist
deformation under high stress (ASM International,
2010). Strength is categorized into tensile, compressive, bending, and
shear strength (Zhang, 2011). Due to resource
limitations, this study focused on compressive strength, which is the ability
of a material to withstand compressive forces without deforming (Betaubun and Hairulla, 2018). It is calculated
using the formula:
Where F is the maximum load (in
Newtons) and A is the total surface area (in mm2).
According to (Zhang, 2011), the strength of a material depends
on its composition and structure. Even with the same composition, materials
with different structures have varying strengths. Other factors include testing
conditions, size, shape, surface characteristics, water content, loading speed,
ambient temperature, and the accuracy of testing equipment. Therefore,
materials are expected to meet specified standards, such as the Indonesian
National Standard (SNI) or equivalent benchmarks, to be deemed suitable for use
(BSN, 2019).
Case
study and material testing were conducted to achieve the study objective. Case
study was specifically conducted to examine the location, earthquake
characteristics, building conditions in the affected area, the types and
quantities of remaining earthquake waste materials, and the state of temporary
housing structures at the site. Meanwhile, material testing included selecting
samples for examination, identifying new materials for comparison, adjusting
sample sizes for testing, and conducting compressive strength tests (Figure 1).
Figure 1 Workflow
of the study
Data collection for material measurement
and testing was carried out using specific tools, including a meter for
measuring dimensions and a compressive test machine for determining compressive
strength values (Table 1).
Table 1 Measurement Framework
2.1. Case Study
The
case study location was the earthquake epicenter in Cianjur, specifically
Sarampad Village, Cugenang District, Cianjur Regency, West Java. This region
was highly earthquake-prone, with an MMI scale greater than VIII, showing the
potential for ground cracks, slope movement, and land shifts (PVMBG, 2014). The earthquake occurred on November
21, 2022, with a magnitude of 5.6 and a damage intensity of VIII on MMI scale (Putratama, 2022). After a year of recovery,
various facilities were constructed in the affected area. This site currently
includes a nearby post and a 3,546.82 m² landfill designated for disaster waste
disposal (Figure 2). Other facilities, such as schools and mosques, had also
been established. The earthquake caused significant damage and loss of life.
According to (Asmarini, 2022), 268 people
died, 1,083 were injured, and 58,362 were displaced due to structural damage.
Moreover, the destruction spanned three regions and sub districts, with 21,282
houses damaged, including 6,570 suffering severe destruction. To aid disaster
victims, several shelters, mosque facilities, and schools have been rebuilt.
Recycle House Program (RHP), led by Mr. Sunaryo Adhiatmoko, was selected as the
focus of this case study. The program conceptualized house reconstruction
post-earthquake using recycled materials (Figure 3).
Figure 2 Landfill
for disposing disaster waste
Figure 3 Recycle
House in Sarampad Village
Figure 4 Exploded Axonometric
of Recycle House Program Materials Component
Table 2 provides an overview of disaster
waste materials that can be repurposed for shelter based on case study and
theoretical investigations. Meanwhile, Figure 5 presents the practical
application of these materials in RHP case study. Examples include mixed
ceramic shards and bricks used for walls, repurposed wooden window and door
frames, and reused roof tiles. Based on the types of materials identified at
the site, specific waste materials were selected for testing. The selection
process considered the application in RHP, use in residents' houses
incorporating disaster waste, the availability of comparative materials, and
the accessibility of testing equipment. The selected materials for testing
included red bricks, roof tiles, and ceramic tiles.
Table 2 Comparison
of Waste Material Application at Location and Theoretical Study
Material Type |
Source | ||||
(PMI, 2019) |
(MSB and JEU, 2011) |
(UNEP, 2008) |
RHP shelter Case Study |
| |
Vegetation |
- |
As compost |
- |
Vegetation |
|
Wood |
Reused as construction |
Reused as furniture or fuel for cooking |
Reused as construction |
Reused as window frame |
|
Bricks |
Reused as construction |
Reused as walls |
Bricks |
Reused as construction |
|
Concrete |
- |
- |
- |
Reused as walls or foundation |
|
Plastic |
- |
Sorted and sold. Cannot be reused |
Recycle |
Collected and transferred |
|
Sand & Gravel |
As aggregate | ||||
Roof tile |
Reused as roof |
- |
- |
Reused as roof |
|
Steel |
Reused as joints |
Recycle as metal strap |
Cannot be reused. Not friendly to victims |
Steel |
|
PVC pipe |
Reused as water Pipes |
- |
- |
- |
|
Glass |
- |
Recycled |
- |
| |
Alumunium |
- |
- |
Recycled | ||
Ceramic tile |
- |
- |
Reused as construction |
Reused as floor tiles |
|
*Note: - not mentioned
Figure 5 Application of
Disaster Waste Material in Recycle House Program and Residents Houses
2.2. Material
Testing
Table 3 The
Tested Materials
*Note: BML = bricks from disaster waste
material; BMB = bricks from new building material; GKL = roof tile from
disaster waste material; GKB = roof tile from new building material; KB =
Ceramic tile from disaster waste material; KL = Ceramic tile from new building
material.
The compressive strength results
required data processing. Therefore, force measurements obtained were converted
into newtons (N), and the materials area into square millimeters (mm²). Using
Equation 1, compressive force (F) was calculated and expressed in megapascals
(MPa) or (N/mm2). Furthermore, Table 4 presents GKB’s fractured texture
compared to GKL’s more robust composition, contributing to the observed
strength disparity.
Table 4 The
Condition of Material Test Results
3.1. BML and BMB Red Bricks Results
Figure 7 BML and BMB Compressive Test Results: Compressive stress–strain
curve (a), Compressive strength value (b)
Bricks Type |
Method |
Test Speed
(mm/min) |
Shape |
Width (mm) |
Length (mm) |
Area (mm2) |
Load (N) |
Height (cm) |
BML |
Flattening |
20.00000 |
plate |
52.8 |
50 |
2640 |
9100.57 |
5 |
BMB |
Flattening |
20.00000 |
plate |
51.3 |
52.2 |
2678 |
34656.7 |
4 |
3.2. GKL and GKB Roof Tile Results
Figure
8(b) shows the compressive strength results for roof tiles, showing significant
differences between samples. Roof tiles made from disaster waste materials
(GKL) showed a compressive strength of 21.8 Mpa, much higher than that of new
roof tiles (GKB) at 1.16 Mpa. This phenomenon could be attributed to load
differences. Table 6 shows GKL with a load value of 55.809 N, significantly
greater than GKB’s load, resulting in higher compressive strength for GKL.
Figure 8(a) further explains this phenomenon, as GKB’s force curve was smaller
and had a faster crack than GKL. However, the cause of the very different
compressive strength values needs further investigated.
Figure 8 GKL and GKB
Compressive Test Results: Compressive stress–strain curve (a), Compressive
strength value (b)
Table 6 GKL and GKB
Roof Tile Compressive Strength Results
Bricks Type |
Method |
Test Speed
(mm/min) |
Shape |
Width (mm) |
Length (mm) |
Area (mm2) |
Load (N) |
Height (cm) |
GKL |
Flattening |
20.00000 |
plate |
49.4 |
51.7 |
2554 |
55809.6 |
1.5 |
GKB |
Flattening |
20.00000 |
plate |
50.6 |
55.4 |
2803 |
3255.81 |
1 |
3.3. KL and KB Ceramic Tile Results
Figure 9 KL and KB Compressive Test Results: Compressive stress-strain curve (a), Compressive strength value (b)
Table 7 KL and KB Ceramic Tile Compressive Strength Results
Bricks Type |
Method |
Test Speed
(mm/min) |
Shape |
Width (mm) |
Length (mm) |
Area (mm2) |
Load (N) |
Height (cm) |
KL |
Flattening |
20.00000 |
plate |
53.20 |
53,10 |
2825 |
50190.4 |
1 |
KB |
Flattening |
20.00000 |
plate |
52.5 |
52,6 |
2762 |
76933.2 |
0.5 |
3.4. Comparison
of Compressive Strength Test Results with Standard
The test results were compared with the compressive strength standards,
as shown in Tables 8, 9, and 10. The comparison showed that BML did not meet
the standards outlined in (SNI-15-2094, 2000)
and (ASTM C62, 2018), while BMB did. GKL satisfied
the standards provided by (Akinwande et al.,
2021) and (Rajalakshmi R., 2020) but
GKB did not. KL did not meet the standards from (CES
Edu Pack Software, 2013) but complied with (ASTM
C 1424, 2019). Lastly, KB met the compressive strength standards
specified in both references. Based on this analysis, disaster waste materials
deemed suitable for shelter construction were KL and GKL. However, further
investigation was required to address materials that did not meet the
standards.
Table 8 Comparison of BML and BMB
Compressive Strength Results with Standards
Red Bricks Type |
Compressive Strength Test Value |
Source | ||
(CES
Edu Pack Software, 2013) |
(SNI-15-2094,
2000) |
(ASTM
C62, 2018) | ||
20 - 50 Mpa |
5-15 Mpa |
8.6 - 20 Mpa | ||
BML |
3.44 Mpa |
Not qualify |
Not qualify |
Not qualify |
BMB |
12.94 Mpa |
Not qualify |
Qualify |
Qualify |
Roof Tile
Type |
Compressive
Strength Test Value |
Source | |
(Akinwande
et al.,
2021) |
(Rajalakshmi
R., 2020) | ||
18.3 Mpa |
8-10 Mpa | ||
GKL |
21.8 Mpa |
Qualify |
Qualify |
GKB |
1.16 Mpa |
Not qualify |
Not qualify |
Table 10 Comparison of GKL and GKB
Compressive Strength Results with Standards
Ceramic Tile
Type |
Compressive
Strength Test Value |
Source |
|
(CES
Edu Pack Software, 2013) |
(ASTM
C 1424, 2019) |
||
20 - 50 Mpa |
3.49-6.4 Mpa |
||
KL |
17.7 Mpa |
Not qualify |
Qualify |
KB |
27.8 Mpa |
Qualify |
Qualify |
In conclusion, evaluating disaster waste materials for reuse and recycling into shelter required careful consideration. Therefore, waste materials should be categorized into groups such as plant materials, soil, domestic waste, and construction materials. At earthquake sites, the remaining materials often included building debris, sediment, plants, and hazardous substances like asbestos. Materials suitable for shelter included bricks for walls, concrete for walls and foundations, wood for furniture and window frames, ceramic tiles for roofing and flooring, as well as sand and gravel for aggregates. One important parameter for reusing disaster waste as shelter material was strength. Compressive strength tests showed that GKL and KL met the required standards with values of 21.8 MPa and 17.7 MPa, respectively. However, BML did not meet the standards, with a value of 3.44 Mpa. These results showed disaster waste materials could be reused for shelter construction, provided the required material and structural standards were met. This experiment was limited to testing compressive strength. Therefore, further investigations were required to explore the broader use of disaster waste materials, specifically for shelter, and to evaluate other types of disaster waste materials other than the three materials tested. Other parameters besides compressive strength should also be examined to ensure a comprehensive assessment of materials suitability.
This study was funded by the Directorate of Research and Development, Universitas Indonesia under Hibah PUTI 2024 (Grant No. NKB-514/UN2.RST/HKP.05.00/2024) awarded to Dr. Miktha Farid Alkadri, S.Ars., M.Ars.
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