| Literature DB >> 36193402 |
Abstract
In recent years, in the process of promoting prefabricated buildings, problems such as waste of resources and energy have been present, which have seriously hindered the realization of carbon emission reduction benefits of prefabricated buildings. Especially during the materialization stage of prefabricated buildings which involves the most engineering activities and the most extensive sources of carbon emissions, it is urgent to further meet the low-carbon development of the construction industry. This study takes the 4 substages of design and development, component production, transportation, and installation during the materialization stage as the point of penetration and identifies the carbon reduction impact pathways based on the 3E (Environment-Economy-Energy) system theory in 5 dimensions: government policy, management mode, technology level, economy input, and energy structure. The data are collected through the questionnaire survey, and structural equation modeling (SEM) is utilized to examine the hypothesis and impact dimensions of the study. The results confirm that the management mode has the strongest effects on carbon emission reduction, followed by government policy, economy input, and technology level, and the energy structure has the weakest effects. This study presents the key carbon reduction pathways during the materialization stage of prefabricated buildings and provides recommendations for different participants to optimize policy guidance, strengthen management supervision, accelerate technology research and development, increase economy input, and optimize energy structure, with a view to achieving low-carbon governance capacity, management mode, technology system, capital, and energy utilization, and also enriches the theory in the field of prefabricated buildings carbon emission reduction, which can better achieve low-carbon development of prefabricated buildings.Entities:
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Year: 2022 PMID: 36193402 PMCID: PMC9526549 DOI: 10.1155/2022/9721446
Source DB: PubMed Journal: J Environ Public Health ISSN: 1687-9805
Figure 1Logic diagram of research methods.
Figure 2Scoping of carbon emission reduction during the materialization stage of prefabricated buildings based on 3E.
List of influencing factors of carbon emission reduction during the materialization stage of prefabricated buildings.
| Dimension | Substage | Descriptions | References |
|---|---|---|---|
| Government policy (PO) | Design and development stage | Government departments provide financial subsidies to departments that adopt low-carbon design solutions (PO1) | [ |
| Production stage | Tax breaks by government departments for component manufacturers that meet carbon emission standards (PO2) | ||
| Transportation stage | Government departments set carbon emission standards and implement incentives and penalties for different sizes of components and different modes of transportation (PO3) | ||
| Installation stage | Government departments set carbon emission standards and implement incentives and penalties for construction sites of different sizes (PO4) | ||
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| Management mode (MA) | Design and development stage | Design and development units cultivate low carbon and environmental awareness among professionals (MA1) | [ |
| Production stage | The enterprises set consumption standards for the production of unit parts and implement them to individuals (MA2) | ||
| Component manufacturers require production workers to meet proficiency standards for operating low-carbon equipment and technology (MA3) | |||
| Transportation stage | Flexible selection of low-carbon and energy-saving loading and unloading solutions according to the size and other characteristics of the parts during transportation (MA4) | ||
| Fully consider the transportation route height limit, load limit, and other factors, and set a low-carbon feasible transportation plan for the transportation of components (MA5) | |||
| Installation stage | Contractors reduce unnecessary waste by optimizing the scheduling plan for manpower, materials, and machinery at the construction site (MA6) | ||
| Contractors reasonably arrange the stacking position of the components to avoid secondary transportation (MA7) | |||
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| Technology level (TE) | Design and development stage | Incorporate low-carbon technologies such as the Internet of Things (IoT) into design solutions (TE1) | [ |
| Production stage | Component manufacturers rely on technologies such as 3D printing and BIM to ensure the quality of components to reduce waste (TE2) | ||
| Component manufacturers use technologies such as robotic production to standardize the production process of components (TE3) | |||
| Installation stage | Contractors adopt advanced recycling technologies for waste components and materials to reduce construction waste generation (TE4) | ||
| Contractors apply low-carbon advanced component connection technology to reduce on-site pouring (TE5) | |||
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| Economy input (EC) | Design and development stage | Investing funds to accelerate new energy and technology research and development (EC1) | [ |
| Production stage | Introduction of advanced energy-saving production equipment by component manufacturers (EC2) | ||
| Transportation stage | Component transport units adopt new transport methods that use clean energy (EC3) | ||
| Installation stage | Contractors introduce advanced energy-saving construction equipment (EC4) | ||
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| Energy structure (EN) | Design and development stage | Design and development units incorporate the use of clean energy as a power source into the design solution (EN1) | [ |
| Production stage | Component manufacturers optimize the structure of materials used for high carbon emission components (EN2) | ||
| Installation stage | Contractors choose to use of building materials with carbon sequestration effect (EN3) | ||
Basic information of interviewees.
| Variable | Description | Number | Percent | Variable | Description | Number | Percent |
|---|---|---|---|---|---|---|---|
| Gender | Male | 158 | 72% | Age | 18-35 years old | 84 | 38% |
| Female | 62 | 28% | 36-50 years old | 97 | 44% | ||
| Educational background | College | 23 | 11% | >50 years old | 39 | 18% | |
| University | 139 | 63% | Nature of work units | Component manufacturers | 51 | 23% | |
| Postgraduate or higher | 58 | 26% | Developers | 37 | 17% | ||
| Working experience | <3 years | 43 | 19% | Contractors | 46 | 21% | |
| 3-5 years | 121 | 55% | Design units | 33 | 15% | ||
| 6-10 years | 48 | 22% | Supervisory units | 24 | 11% | ||
| >10years | 8 | 4% | Scientific institutions and universities | 29 | 13% |
The index system of the influencing factors of carbon emission reduction during the materialization stage of prefabricated buildings.
| Dimension | Code | Mean value | Standard deviation | CITC | Cronbach's alpha | KMO |
|---|---|---|---|---|---|---|
| PO | PO1 | 3.65 | 0.989 | 0.681 | 0.864 | 0.861 |
| PO2 | 3.30 | 0.976 | 0.809 | |||
| PO3 | 3.72 | 0.993 | 0.659 | |||
| PO4 | 3.64 | 0.991 | 0.678 | |||
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| MA | MA1 | 3.77 | 0.818 | 0.650 | 0.905 | 0.895 |
| MA2 | 3.72 | 0.811 | 0.708 | |||
| MA3 | 3.55 | 0.851 | 0.750 | |||
| MA4 | 3.90 | 0.787 | 0.629 | |||
| MA5 | 3.90 | 0.808 | 0.659 | |||
| MA6 | 3.26 | 1.065 | 0.736 | |||
| MA7 | 3.81 | 0.792 | 0.689 | |||
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| TE | TE1 | 3.70 | 0.807 | 0.638 | 0.875 | 0.843 |
| TE2 | 3.78 | 0.848 | 0.658 | |||
| TE3 | 3.67 | 0.801 | 0.725 | |||
| TE4 | 3.82 | 0.813 | 0.633 | |||
| TE5 | 4.09 | 0.871 | 0.491 | |||
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| EC | EC1 | 3.50 | 0.797 | 0.616 | 0.931 | 0.821 |
| EC2 | 3.97 | 0.779 | 0.572 | |||
| EC3 | 3.90 | 0.791 | 0.579 | |||
| EC4 | 3.84 | 0.800 | 0.590 | |||
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| EN | EN1 | 3.31 | 1.005 | 0.696 | 0.832 | 0.712 |
| EN2 | 3.69 | 1.023 | 0.522 | |||
| EN3 | 3.63 | 0.884 | 0.523 | |||
Figure 3Standardized factors loadings and path coefficients of the first-order SEM.
The fit indices of the first-order SEM.
| Index | Estimation | Standard | Result |
|---|---|---|---|
|
| 2.209 | (1, 3) | Accept |
| RMSEA | 0.074 | <0.08 | Accept |
| RMR | 0.044 | <0.5 | Accept |
| CFI | 0.923 | >0.9 | Accept |
| TLI | 0.912 | >0.9 | Accept |
| IFI | 0.924 | >0.9 | Accept |
| PGFI | 0.663 | >0.5 | Accept |
| PNFI | 0.759 | >0.5 | Accept |
Standardized path coefficients and hypothesis testing of the first-order SEM.
| Hypothesis | Relationship | Estimate | S.E. | C.R. |
| Support |
|---|---|---|---|---|---|---|
| H1 | PO⟶MA | 0.717 | 0.079 | 8.677 | ∗∗∗ | Yes |
| H2 | PO⟶EC | 0.135 | 0.127 | 1.487 | 0.137 | No |
| H3 | PO⟶EN | 0.054 | 0.091 | 0.579 | 0.562 | No |
| H4 | PO⟶TE | 0.028 | 0.089 | 0.314 | 0.753 | No |
| H6 | MA⟶EC | 0.603 | 0.144 | 6.168 | ∗∗∗ | Yes |
| H7 | MA⟶EN | 0.449 | 0.119 | 3.843 | ∗∗∗ | Yes |
| H8 | MA⟶TE | 0.574 | 0.120 | 5.023 | ∗∗∗ | Yes |
| H10 | EC⟶TE | 0.219 | 0.059 | 2.671 | 0.008∗∗ | Yes |
| H11 | EC⟶EN | 0.268 | 0.061 | 3.033 | 0.002∗∗ | Yes |
∗ p < 0.05, ∗∗p < 0.01, and∗∗∗p < 0.001.
Figure 4Standardized factor loadings and path coefficients of the second-order SEM.
The fit indices of the second-order SEM.
| Index | Estimation | Standard | Result |
|---|---|---|---|
|
| 2.178 | (1, 3) | Accept |
| RMSEA | 0.073 | <0.08 | Accept |
| RMR | 0.044 | <0.5 | Accept |
| CFI | 0.923 | >0.9 | Accept |
| TLI | 0.914 | >0.9 | Accept |
| IFI | 0.924 | >0.9 | Accept |
| PGFI | 0.673 | >0.5 | Accept |
| PNFI | 0.772 | >0.5 | Accept |
Standardized path coefficients and hypothesis testing of the second-order SEM.
| Hypothesis | Relationship | Estimate | S.E. | C.R. |
| Support |
|---|---|---|---|---|---|---|
| H5 | PO⟵CA | 0.746 | 0.048 | 9.735 | ∗∗∗ | Yes |
| H9 | MA⟵CA | 0.923 | 0.047 | 11.458 | ∗∗∗ | Yes |
| H12 | EC⟵CA | 0.775 | 0.052 | 9.761 | ∗∗∗ | Yes |
| H13 | EN⟵CA | 0.738 | 0.059 | 11.425 | ∗∗∗ | Yes |
| H14 | TE⟵CA | 0.801 | 0.053 | 8.543 | ∗∗∗ | Yes |
∗ p < 0.05, ∗∗p < 0.01, and∗∗∗p < 0.001.
Figure 5The influence between carbon emission reduction dimensions.
Figure 6Determine the key carbon emission reduction path in the physical and chemical stage of prefabricated buildings.
Figure 7Carbon reduction path implementation for participants involved during the materialization stage of prefabricated buildings.