Abstract
Numerous care and procedures have been declared to address the problem of global warming and building construction emissions, all to minimise the health negativities that arise due to high pollution levels. Construction markets are now more awake to sustainability accomplishments; thus, it is vital to educate construction stakeholders on preferred natural or alternative materials for construction purposes based on their significance to sustainable development. This paper is aimed at conducting a structured literature review on the subject of particle emissions of natural and alternative building materials and to provide an overview of the associated health challenge. Documentary data on particulate matter emissions of these materials were collected through desk research. The study showed that the problem of selecting good quality material with emission-free health challenges stems from the fact that the built environment professional has little clue of knowing about the toxicity of building materials. Throughout the review, literature has been quiet on the emissions of PM10 and PM2.5 released from the use of both natural and alternative materials, thus calling for concern and a more significant research direction towards the study of this phenomenon to yield the required results.
Access provided by Autonomous University of Puebla. Download conference paper PDF
Similar content being viewed by others
Keywords
1 Introduction
Pollution characterised by building construction material emissions has become a hot spot of study due to its accompanying environmental and health complexities. This research aims to conduct a structured literature review on the subject of particle emissions of natural and alternative building materials. The high demand for construction materials is dependent on consumption of raw materials (Lassio and Naked, 2016). The difficulty of determining the pattern of toxins emitted from the use of building construction materials by the built environment professional has led to the use of several toxic materials which are worthy of attention. Some of these materials are legally accepted, yet they contain some form of toxicity (Levin, 2016; Pacheco-Torgal & Jalali, 2011). Thus, there is the need for environmental assessment of building materials so as to substitute those prone to health ramifications with more environmentally friendly ones in the delivery of sustainable building construction projects (Farahzadi et al., 2016).
In their study of building material emissions through regression, He et al. (2005) argued that emission parameters have a causal connection between the molecular structure of compounds and material properties. Their study explained that the two most widely accepted physical models for emission determination are (1) the diffusion coefficient [D] and (2) the partition coefficient [K]. Thus, many researchers use Fick’s law to interpret the mass transfer inside the material due to the concentration difference. The argument by He et al. (2005) was affirmed by the research carried out by Zhang et al. (2018, p.3) – through material efficiency by separation and dematerialisation. The material efficiency measurements ‘include all changes that result in decreasing the number of materials used to produce one unit of economic output or to fulfil human needs’.
To be able to assess the emission characteristics of building construction materials, there is a need to determine the emission factors and the taxonomy of chemicals emitted concerning the materials’ health intricacies. Analysing the search results from a bibliometric review, an overview of natural and alternative material emissions is presented in this paper with discussions and pathway for future research.
The procedure involved a detailed literature review of building construction materials to provide a summary of existing studies of particle emissions. The literature is relative to the health implications of the materials in question that apply to the built environment. The study depended on those building construction materials available on the market with emission quality deductions and consisted of three stages.
Stage 1 consisted of articles retrieved from reputable databases from a list of publications using the keywords as the benchmark. Further, articles from each database were grouped and sorted based on their relevance to the objectives of the study. In stage 2, a systematic review of the articles (peer-reviewed journals, original industry reports) and books to solicit for the data of particulate matter emissions of building construction materials and their health benefits and/or challenges was carried out. Critical reading was carried out to obtain evidence and to provide a useful evaluation of the text. Stage 3, the final stage, considered the impact of emissions on human health from literature.
2 Search Strategy
The scope of the literature search was within the confines of the widely academically recognised databases, namely, Google Scholar, ScienceDirect, ResearchGate and Web of Science. The literature was then sorted according to their background, for example, Journal of Cleaner Production (JCP) , Multidisciplinary Digital Publishing Institute (MDPI), ResearchGate and Original Industry Reports and Letters. The studies that did not connate to the objectives of the review were removed. The literature retrieval was done using the keywords and Boolean logical operators – for example, natural and alternative building material emissions. Sources of literature that had strong affinity to the study theme were used as a foundation for the review (Ramdhani et al., 2014). Also, particulate matter emissions, factors affecting material emissions and building construction material efficiency were included in the search plan as text words. To ensure that high-quality literature was used, refereed journals and original documents were selected for the study (Wallace & Wray, 2013).
2.1 Frontline Literature
A total of 127 journal articles, industry reports, letters and unpublished articles were retrieved from various databases. Following Sun et al. (2020) and Chan et al. (2020) study, a scrutiny of all the articles was carried out. Repeated articles were removed and those articles with the required relevance to the study were selected. After this consideration, a total of 107 articles remained. With the need for more relevance, a comprehensive examination of abstracts, conclusions and full-text analysis was carried out. After the examination of the abstracts, conclusions and text analysis, 53 of the articles found to be relevant to the research were collected for further studies. Seven out of the 53 publications were deemed to be most relevant to the study and were captioned ‘frontline literature’, and they were used as the basis for the literature synthesisation. Table 37.1 shows the keywords setting used for the search. Table 37.2 shows the spread across various search results of the final literature. Table 37.3 clarifies the synthesised matrix organised by frontline literature (Fig. 37.1) .
3 Family of Construction Materials
3.1 Natural Materials (Traditional)
In their study of building material emissions for the construction of classrooms, Moulton-Patterson et al. (2003) classified ‘commonly used building products containing low or no recycled content’ as standard or natural materials. When the working life of construction material is increased, the eco-friendliness of the content is improved (Edwards and Bennett, 2003; Hertwich et al., 2019). In their study of material efficiency, Ruuska and Häkkinen (2014, p. 267) argued that the use of natural materials supports the quality of life of the occupiers of the building. They posit that the ‘natural building material that has the required emission stipulations provides a better construction option and also reduces emission’. Natural materials are found as either renewable or non-renewable. The renewable materials are those that can be replenished after harvesting, while the non-renewable material resource is those that can only be gathered once. The theory of durability concerning material efficiency was corroborated by Lifset and Eckelman (2013) and Levin (2016). In his plenary architecture lecture, Levin (2016, p.15) explained, ‘selecting natural building materials that are durable has sufficiently environmental benefits than the one that must be substituted more than once in the life of the building’. For example, when the concrete cover is doubled from 10 mm to 20 mm, the service life of reinforcement – ‘defined as the time it takes carbonation to reach the reinforcement’, Levin (2016, p. 63) – is increased by 400% but increases concrete consumption by only 5–10%. Farahzadi et al. (2016) proposed a variety of conventional construction materials: viz. standard bricks, oil paint, aluminium frames, polystyrene thermal insulation and air-filled double glazed windows.
3.2 Alternative Materials
Moulton-Patterson et al. (2003) carried out an extensive study on material emissions for the construction of schools in the United States. During their study, they classified alternative materials as those with ‘higher amounts of recycled content, rapidly renewable materials, and/or products containing no or low volatile organic compounds – VOCs’ (p. 1). However, in their study of the assessment of alternative materials, Farahzadi et al. (2016) also established the following materials as being alternative construction materials, thus clay blocks, glass wool thermal insulation, acrylic paint, wooden frames and argon-filled double glazed windows. In his study of building ecology (design alternatives), Levin (2016, p. 7) characterised building materials as one of the essential primary criteria for classifying a building as either healthy or not. The trade-offs in using alternative building construction material are to accomplish the expected results. The optimum way of doing this is ‘to select low emitting products, to condition or treat the product before installation or to ventilate the building after installation before occupancy’.
To this effect, the most prudent way of reducing environmental pollution from building construction materials and thus raise its efficiency is to use them again at the end of their useful life to prevent them from going through the processes of extraction to processing (Hertwich et al., 2019) (Table 37.4).
After Farahzadi et al. (2016)
4 Natural and Alternative Material Selection
In their study of validating a set of empirically weighted sustainability indicators for construction products, Ghumra et al. (2011) posit that pollution from the use of the construction materials was highest on the ranking of all indicators. Life cycle assessment (LCA) has the most significant attention based on the indicators’ respective weightings used in their study. Even though LCA is a widely accepted criterion in the promotion of sustainable material selection, the process is intensive and difficult to handle. Upstill-Goddard et al. (2015) argue that those responsible for material selection may choose other methodology and still aim for higher performance. To this effect, Upstill-Goddard et al. (2015) suggest that LCA methodology should be carried out and promoted as a separate entity.
Khoshnava et al. (2018) conclude that the action of building material selection involves a complex challenge which usually looks at quality, performance, beauty and cost to reveal the main serviceability functions. In selecting building materials, whilst the focus is usually on the environmental impact reduction, it is imperative to consider the economic and social impacts as well. The emission characteristics which contribute to human health efficiency are considered under social impact.
5 Particulate Matter (PM) Emissions
Particulate matter emissions are characterised by the presence of small particles and liquids.
Depending on their size, particles can be inhaled deeper into different parts of the respiratory system causing serious health challenges.
Doroudiani et al. (2012, p. 264) investigated the toxic release from construction materials during fire. The authors reported in their study that ‘particle size larger than 5μm are filtered in the upper respiratory system while the smaller ones can travel to bronchial and alveolar areas’.
In their study on cities’ ambient particulate matter source contribution Karaguliana et al. (2015) and Bylone (2019) clarified that as of year 2015, PM was judged to be the core function for health effects of pollution.
5.1 Emissions and Human Health
Pacheco-Torgal and Jalali (2011, p. 2) substantiated that a large number of building construction materials exhibit some form of toxicity, ‘thus causing several health-related problems such as asthma, itchiness, burning eyes, skin irritations or rashes, nose and throat irritation, nausea, headache, dizziness, fatigue, reproductive impairment, disruption of the endocrine system, impaired child development and birth defects, immune system suppression and cancer’. Table 37.5 shows some cancer-causing agents and their likely sources from paints used in the building industry.
The global burden of disease (GBD) reported in 2015 that air pollution is the fifth-ranked mortality factor (Burnett et al., 2018).
During a fire, significant toxic chemicals are emitted from building materials. These chemicals released are very harmful to human health (Doroudiani et al., 2012). Considering Doroudiani et al. (2012) study and GBD (2015) report, it is imperative that emissions from both the usage of materials and their combustion properties are taken into account during selection of natural and alternative materials for construction projects.
5.2 Factors Affecting Building Material Emissions
The detailed study carried out by Moulton-Patterson et al. (2003) outlined certain critical factors that affect the emissions from materials. Examples of these factors include:
-
Quantity of material used in a particular operation.
-
The assumed average ventilation rate.
-
The time between completion of construction and occupancy.
-
Building ventilation rate before and during occupancy.
-
Age of material between manufacturing and installation.
-
Storage, delivery and construction practices.
These factors critically affirm that material efficiency has a larger role to play in terms of emissions. This means emission of a material is a direct function of the quantity of material and its concentration present in a product which affirms Fick’s law .
6 Material Efficiency
Holton et al. (2008) emphasise the role of responsible material sourcing leading to enhanced material selection through material efficiency to provide an avenue to unlock opportunities to improve competitiveness.
In this perspective, Glass (2011) argued that responsible sourcing in industrial procurement practice is a challenge to selecting sustainable efficient materials. The study explains that for selecting an efficient construction material, there is the need to be proactive rather than reactive. ‘The construction industry’s fragmented supply network is a fundamental problem’ (Glass, 2011, p. 169). Zhang et al. (2018) established that eco-friendly indicators emphasise the environmental reduction of resource use. The study by Ruuska and Häkkinen (2014), Edwards and Bennett (2003) and Hertwich et al. (2019) corroborates to the assertion that the durability and longevity of a material contribute to its eco-friendliness and thus its efficiency.
7 Conclusion and Future Research Direction
Motivated by building material emissions and their accompanying health complexness, this study concentrated on the need for insight into particle emissions of both natural and alternative building materials as directions for sustainable built environment achievement. The literature was sorted and categorised to help understand the pathway to the study of material emissions in the academic fraternity. A list of the important databases with their brief research engagement helped to outline the scope of this review. Durability and longevity of construction materials appear to be very significant in the study of construction material selection as corroborated by the study carried out by Ghumra et al. (2011).
The problem of selecting good quality material with emission-free health challenges stems from the fact that the built environment professionals have little clue of knowing about the toxicity of building materials. Throughout the review, literature has been quiet on the emissions of PM10 and PM2.5 released from the use of both natural and alternative materials. This calls for concern, and a more significant research direction is required towards the study of this phenomenon to yield the required data that is essential for analysing the health complexities accompanying the use of these construction materials. Alternatively, the review confirms several studies on emissions relative to carbon and volatile organic compounds on building materials.
The study has been limited because to ascertain a more in-depth theoretical account, detailed analysis and discovery are paramount to bring forwards the boundary of emissions between natural and alternative materials.
Future research pathway(s) should provide more information on particulate matter emissions (PM10, PM2.5) of building construction materials with various quantitative emission factors of both natural and alternative materials.
Responsible material sourcing has also been found as an enhanced methodology to promote the mitigation of challenges associated with material selection. To this effect, even though life cycle assessment methodology is cumbersome, it provides a better inclusion in responsible sourcing (ethical management of sustainability issues within the construction supply chain) to demonstrate transparency with regard to the materials within a particular product, and thus aids in their selection.
When this is done, the confidence for material selection will be expanded to enable the built environment professional to make bold and knowledgeable decisions in this direction.
References
Aisyah, S., Rohana, S., Herberd, A., Zainuddin, A., Armi, M. (2019). Exposure of particulate matter 2.5 (PM2.5) on lung function performance of construction workers. In AIP Conference Proceedings 2124 (020030). AIP Publishing, pp. 1–8.
Aoki, T., & Tanabe, S. (2007). Generation of sub-micron particles and secondary pollutants from building materials by ozone reaction. Atmospheric Environment, 41(15), 3139–3150. https://doi.org/10.1016/j.atmosenv.2006.07.053.
Azari, R. (2014). Integrated energy and environmental life cycle assessment of office building envelopes. Energy and Buildings, 82, 156–162. https://doi.org/10.1016/j.enbuild.2014.06.041.
Baetens, R., Jelle, B. P., & Gustavsen, A. (2010). Phase change materials for building applications: A state-of-the-art review Phase Change Materials for Building Applications. SINTEF, 42, 1361–1368.
Bellis, L. D. E. (1998). Material Emission Rates Literature Review, and the Impact of Indoor Air Temperature and Relative Humidity, 33(5), 261–277.
Burnett, R., Chen, H., Szyszkowicz, M., Fann, N., Hub-bell, B., Pope, C. A., et al. (2018). Global estimates of mortality associated with long-term exposure to outdoor fine particulate matter. Proceedings of the National Academy of Sciences, 115(38), 9592–9597.
Bylone, M. (2019). Healthy work environment 101. AACN Advanced Critical Care, 22(1), 19–21. https://doi.org/10.1097/NCI.0b013e3182049053.
Chan, A. P. C., Tetteh, M. O., & Nani, G. (2020). Drivers for international construction joint ventures adoption: A systematic literature review. International Journal of Construction Management, 10(2), 1–13. https://doi.org/10.1080/15623599.2020.1734417.
Cheriyan, D., & Choi, J. (2020). A review of research on particulate matter pollution in the construction industry. Journal of Cleaner Production, 254. https://doi.org/10.1016/j.jclepro.2020.120077.
Chin, K., Laguerre, A., Ramasubramanian, P., Pleshkov, D., Stephens, B., & G. E. (2019). Emerging investigator series: Primary emissions, ozone reactivity, and byproduct emissions from building insulation materials. Environmental Science: Processes and Impacts, 21(8), 1255–1267. https://doi.org/10.1039/c9em00024k.
Doroudiani, S., Doroudiani, B. and Doroudiani, Z. (2012) Materials that release toxic fumes during fire. Toxicity of Building Materials. Woodhead Publishing Limited. doi: https://doi.org/10.1533/9780857096357.241.
Edwards, S., & Bennett, P. (2003). Construction products and life-cycle thinking. Industry and Environment, 26(2–3), 57–61.
Farahzadi, L., Bakhitari, A. L., Gutierrez, U. R., and Azemati, H. (2016). Assessment of alternative building materials in the exterior walls for reduction of operational energy and CO2 emissions assessment of alternative building materials in the exterior walls for reduction of operational energy and CO2 emissions. International Journal of Engineering and Advanced Technology (IJEAT), (September), pp. 0–7.
Ghumra, S., Glass, J., Frost, M., Watkins, M., Mundy, J. (2011). Validating a set of empirically weighted sustainability indicators for construction products Shamir. Materials and Energy Assessment in Ceequal Transport Project, Proceedings in the Institution of Civil Engineers, pp. 153–164.
Glass, J. (2011). Briefing: Responsible sourcing of construction products. In Proceedings of the Institution of Civil Engineers: Engineering Sustainability, pp. 167–170. doi: https://doi.org/10.1680/ensu.1000011.
Gmelin, H., & Seuring, S. (2014). Determinants of a sustainable new product development. Journal of Cleaner Production, 69, 1–9. https://doi.org/10.1016/j.jclepro.2014.01.053.
Gonçalves de Lassio, J. G., & Naked Haddad, A. (2016). Life cycle assessment of building construction materials: Case study for a housing complex TT - Evaluación de ciclo de Vida de materiales de edificaciones: Estudio de Caso en complejo de viviendas. Revista de la construcción, 15(2), 69–77. https://doi.org/10.4067/S0718-915X2016000200007.
Greenstone, M. and Ryan, N. (2020). Continuous Emissions Monitoring Systems (CEMS) in India March 2020 Impact Evaluation Report 111 (March).
Haapio, A., & Viitaniemi, P. (2008). A critical review of building environmental assessment tools. Environmental Impact Assessment Review, 28(7), 469–482. https://doi.org/10.1016/j.eiar.2008.01.002.
Had, L. and Brain, A. (2020). Concrete solutions that lower both emissions and air pollution air quality and climate change intertwine in unexpected ways; a concrete example.
Harb, P., Locoge, N., & Thevenet, F. (2018). Emissions and treatment of VOCs emitted from wood-based construction materials: Impact on indoor air quality. Chemical Engineering Journal, 354(August), 641–652. https://doi.org/10.1016/j.cej.2018.08.085.
He, G., Yang, X., & Shaw, C. Y. (2005). Material emission parameters obtained through regression. Indoor and Built Environment, 14(1), 59–68. https://doi.org/10.1177/1420326X05050347.
Hertwich, Edgar G., Ali, Saleem, Ciacci, Luca, Fishman, Tomer, Heeren, Niko, Masanet, Eric (2019). Material efficiency strategies to reducing greenhouse gas emissions associated with buildings, vehicles, and electronics - A review. Environmental Research Letters.
Holton, I., Glass, J., & Price, A. (2008). Developing a successful sector sustainability strategy: Six lessons from the UK construction products industry. Corporate Social Responsibility and Environmental Management, 15(1), 29–42. https://doi.org/10.1002/csr.
Huang, Kun-chih, Tsay, Shyan-Yaw, Lin, Fang- Ming and Chung, J.-W. (2019). Efficiency and performance tests of the sorptive building materials that reduce indoor formaldehyde concentrations. PLoS ONE.
Hillman, K., Dangaard, A., Ola, E., Jonsson, D., and Fluck, L. (2015). Climate benefits of material recycling, inventory of average greenhouse gas emissions for Denmark, Norway and Sweden. http://dx.doi.org/10.6027/TN2015-547. Available at www.norden.org/nordpub
International Institute of Sustainable Development [IISD]. (2019). Carbon Accounting gaps, Emission, Omissions. Report, (April), pp. 1–74.
Jalali, S. (2015). Toxicity of building materials: A key issue in sustainable construction. (September 2011). doi: https://doi.org/10.1080/19397038.2011.569583.
James, J. P., & Yang, X. (2005). Emissions of volatile organic compounds from several green and non-green building materials: A comparison. Indoor and Built Environment, 14(1), 69–74. https://doi.org/10.1177/1420326X05050504.
Järnström, H. (2007). Reference values for building material emissions and indoor air quality in residential buildings. Finland: VTT Publications.
Jung, S., Kang, H., Sung, S., & H. T. (2019). Health risk assessment for occupants as a decision-making tool to quantify the environmental effects of particulate matter in construction projects. Building and Environment, 161, 1–16.
Karaguliana, F., Belis, C. A., Dora, C. F. C., Prüss-Ustün, A. M., Bonjour, S., Adair-Rohani, H., & Amann, M. (2015). Contributions to cities’ ambient particulate matter (PM): A systematic review of local source contributions at global level. Atmospheric Environment, 120, 475–483.
Keita, Sekou, Liousse, Cathy, Yoboué, Veronique, Dominutti, Pamela, Assamoi, Eric-Michel, Doumbia, Madina, Bahino Julien, Guinot, B. (2018). Particle and VOC emission factor measurements for anthropogenic sources in West Africa. Atmospheric Chemistry and Physics.
Khoshnava, S. M., Rostami, R., Valipour, A., Ismail, M., & Rahmat, A. R. (2018). Rank of green building material criteria based on the three pillars of sustainability using the hybrid multi criteria decision making method. Journal of Cleaner Production, 173, 82–99. https://doi.org/10.1016/j.jclepro.2016.10.066.
Kong, A., Kang, H., He, S., Li, N., & Wang, W. (2020). Study on the carbon emissions in the whole construction process of prefabricated floor slab. Applied Sciences (Switzerland), 10(7). https://doi.org/10.3390/app10072326.
Levin, H. (2016). Building ecology: An architect’s perspective -- plenary lecture. (November 2014).
Lifset, R., & Eckelman, M. (2013). ‘Material efficiency in a multi-material world’, philosophical transactions of the Royal Society A: Mathematical. Physical and Engineering Sciences, 371(1986). https://doi.org/10.1098/rsta.2012.0002.
Magee, R. (2005). A material emission database for 90 target VOCs NRC Publications Archive (NPArC) Archives des publications du CNRC (NPArC) A Material emission database for 90 target VOCs. Won, D. Y.; Magee, R. J.; Yang, W.; Lusztyk, E.; Nong, G.; Shaw, C. (January).
Maoeng, M., Edoun, E. I., & Mbohwa, C. (2020). Sustainable development practices in the south African construction industry: A review of related literature. Applied Sciences, 10, 1418–1426.
Martínez-Rocamora, A., Solís-Guzmán, J., & Marrero, M. (2016). LCA databases focused on construction materials: A review. Renewable and Sustainable Energy Reviews, 58, 563–570. https://doi.org/10.1016/j.rser.2015.12.243.
Meng, J., Liu, J., & Tao, S. (2015). Tracing primary PM2.5 emissions via Chinese supply chains. Environmental Research Letters, 11, 1–13.
Milner, J., Hamilton, I., & Woodcock, J. (2020). Health benefits of policies to reduce carbon emissions. BMJ, 368, 6–11. https://doi.org/10.1136/bmj.l6758.
Mohajerani, A., Siu-Qun, H., Mehdi, M., Arulrajah, A., Horpibulsuk, S., Kadir, M., & Aeslina Farshid, A. T. R. (2019). Amazing types, properties, and applications of fibres in construction materials. Materials, 12(16), 1–45. https://doi.org/10.3390/ma12162513.
Moulton-Patterson, L., Peace, C., & Leary, M. (2003). Building material emissions study. Integrated Waste Management Board, 22, 1–328.
Nwodo, M. N., & Anumba, C. J. (2019). A review of life cycle assessment of buildings using a systematic approach. Building and Environment, 162(July), 100. https://doi.org/10.1016/j.buildenv.2019.106290.
Pacheco-Torgal, F., & Jalali, S. (2011). Toxicity of building materials: A key issue in sustainable construction. International Journal of Sustainable Engineering, 4(3), 281–287. https://doi.org/10.1080/19397038.2011.569583.
Raifman, Matthew, Russell, Armistead, Skipper, Nash, Kinney, P. (2020) ‘Quantifying the health impacts of eliminating air pollution emissions in the City of Boston’, Environmental Research Letters 24 1–19.
Ramdhani, A., Ramdhani, M., & Amin, A. (2014). Writing a literature review research paper: A step-by-step approach. International Journal of Basic and Applied Science, 3(01), 47–56.
Ramesh, T., Prakash, R., & Shukla, K. K. (2010). Life cycle energy analysis of buildings: An overview. Energy and Buildings, 42(10), 1592–1600. https://doi.org/10.1016/j.enbuild.2010.05.007.
Reed, C. H. (2011). Reference material to improve reliability of building product VOC emissions testing. (September), pp. 30–33.
Ruuska, A., & Häkkinen, T. (2014). Material efficiency of building construction. Buildings, 4(3), 266–294. https://doi.org/10.3390/buildings4030266.
Shi, Qingwei, Gao, Jingxin, Wang, Xia, Ren, Hong, Cai, Weiguang, and Wei, H. (2020). Temporal and spatial variability of carbon emission intensity of urban residential buildings: Testing the effect of economics and geographic location in China. Sustainability, Switzerland, pp. 1–23.
Silva, R. V., de Brito, J., & Dhir, R. K. (2019). Use of recycled aggregates arising from construction and demolition waste in new construction applications. Journal of Cleaner Production, 236, 117629. https://doi.org/10.1016/j.jclepro.2019.117629.
SimaPro Library Database Manual Colophon, M (n.d.).
Souza, V., & Borsato, M. (2016). Sustainable design and its interfaces: An overview Vitor de Souza * and Milton Borsato. International Journal of Agile Systems and Management, 9(3), 183–211.
Sun, J., Zhou, Z., Huang, J., & Guoxing, L. (2020). A bibliometric analysis of the impacts of air pollution on children. International Journal of Environmental Research and Public Health, 12, 1–11. https://doi.org/10.3390/su12072695.
United States Environmental Protection Agency. (2013). Recommended procedures for development of emissions factors and use of the WebFIRE Database.
Upstill-Goddard, J., Glass, J., Dainty, A., Nicholson, I. (2015). Analysis of responsible sourcing performance in BES 6001 certificates. In Proceedings of the Institution of Civil Engineers: Engineering Sustainability, pp. 71–81.
Wallace, M., & Wray, A. (2013). Critical Reading and writing for postgraduates, educate~. New Delhi: Sage.
Wegener, A., Sleeswijk, O., van Lauran, G., Jeroen, S., & Jaap, H. M. (2007). Normalisation in product life cycle assessment: An LCA of the global and European economic systems in the year 2000. Science of the Total Environment, 390(1), 227–240.
Wille, K., & Boisvert-Cotulio, C. (2015). Material efficiency in the design of ultra-high performance concrete. Construction and Building Materials, 86, 33–43. https://doi.org/10.1016/j.conbuildmat.2015.03.087.
Xia, B., Ding, T., & Xiao, J. (2020). Life cycle assessment of concrete structures with reuse and recycling strategies: A novel framework and case study. Waste Management, 105, 268–278. https://doi.org/10.1016/j.wasman.2020.02.015.
Zhang, C., Chen, W. and Ruth, M. (2018). Measuring material efficiency: A review of the historical evolution of indicators. Methodologies and Findings. (April). doi: https://doi.org/10.1016/j.resconrec.2018.01.028.
Zhang, J. J. (1997). A review of volatile organics emission data for building materials and furnishings. doi: https://doi.org/10.4224/20338000.
Author information
Authors and Affiliations
Editor information
Editors and Affiliations
Rights and permissions
Copyright information
© 2022 The Author(s), under exclusive license to Springer Nature Switzerland AG
About this paper
Cite this paper
Ansah, N.B., Adinyira, E., Agyekum, K., Aidoo, I. (2022). Bibliometric Study on Particle Emissions of Natural and Alternative Building Materials. In: Gorse, C., Scott, L., Booth, C., Dastbaz, M. (eds) Climate Emergency – Managing, Building , and Delivering the Sustainable Development Goals. Springer, Cham. https://doi.org/10.1007/978-3-030-79450-7_37
Download citation
DOI: https://doi.org/10.1007/978-3-030-79450-7_37
Published:
Publisher Name: Springer, Cham
Print ISBN: 978-3-030-79449-1
Online ISBN: 978-3-030-79450-7
eBook Packages: EnergyEnergy (R0)