Abstract
It has been significant yet challenging to recycle and reuse different kinds of wastes because of their mass production within society. Many efforts have been conducted to reuse wastes in different fields. Interestingly, some wastes have been employed to replace traditional petroleum-based flame retardants for polymeric materials. This review focuses on the recent development of waste flame retardants and their impacts on thermal stability, flame retardancy, and smoke suppression of polymers, followed by representative flame-retardant mechanisms. Finally, the key challenges associated with waste flame retardants are presented, and some future perspectives are proposed.
Introduction
With the development of our society, abundant wastes have been continuously generated in daily life and industrial production, which have led to serious environmental deterioration problems, for example, marine microplastics and global warming. Such issues have driven scientists and engineers to explore how to effectively change waste into wealth. Hence, recent years have witnessed the recycle and reuse of different kinds of wastes in various industrial areas (; ).
The superior chemical resistance, and thermal and mechanical properties of polymeric materials have meant they have ubiquitous applications in modern society (; ; ). However, most of them are highly flammable and produce abundant smoke during combustion, which severely threatens humans and the environment; thus, it is necessary to enhance the fire safety of polymers via adding flame retardants (; ; ). In the past, flame retardants are mainly derived from petroleum resources, which worsen the depletion of fossil resources (). Based on the sustainable development strategy, many wastes have been reused to replace traditional flame retardants recently, and many important outcomes have been reported, demonstrating that the application of some wastes is an effective way to prepare flame-retardant polymeric materials (). For instance, used Bayer red mud to synthesize Mg/Al/Fe-layered double hydroxides (Mg/Al/Fe-LDHs), which were applied in the preparation of flame-retardant ethylene-vinyl acetate (EVA). Their results showed that the limiting oxygen index of the as-prepared EVA can be up to 26.8%. reported a flame-retardant polypropylene (PP) with ammonium polyphosphate (APP), waste-based biochar, and wool. The results showed that both biochar and wool not only improved the flame retardancy of PP but also retained the mechanical properties. Hence, many waste-based flame retardants exhibit obvious flame retardant function towards polymeric materials.
Herein, this review focuses on the recent development of three kinds of common wastes (industrial, domestic, and plant; see Scheme 1) and highlights their influences on the thermal stability, flame retardancy, and smoke suppression of polymeric materials. Additionally, the flame-retardant mechanism of different wastes will be analyzed. Finally, their key challenges and future perspectives will also be indicated.
SCHEME 1
Industrial Waste
With the development of modern production, a constant stream of industrial waste is discharged into the environment, which has been harming the ecosystem and even human health severely. Thus, the reuse of industrial waste has become a hot topic in both academia and industry (). Fortunately, many types of industrial wastes, for example, fly ash, oil sludge, and red mud, contain different valuable flame-retardant ingredients, such as thermally stable SiO2, Al2O3, and Fe2O3, thus exhibiting huge potential in the fabrication of flame-retardant polymers (; ; ). For instance, fabricated a flame-retardant epoxy resin (ER), which contained ammonium tetrafluoroborate (ATFB), aluminum hydroxide (Al(OH)3), and red mud (RM). Obviously, the introduction of ATFB, Al(OH)3, and RM improves the charring capacity of ER (see Figure 1). During the burning process, RM effectively retards the combustion of epoxy matrix due to its abundant Fe, Al, and Si elements. Additionally, the combination of ATFB, Al(OH)3, and RM endows epoxy resin with improved flame retardancy, mechanical properties, and thermal stability (see Figure 2), for example, a limited oxygen index (LOI) of 29.0%, a tensile strength of 112 MPa, and a glass transition temperature (Tg) of 210°C. synthesized an Mg-Al-Fe ternary-layered double hydroxide (LDH) using red mud as a raw material, and the corresponding flame-retardant and thermally stable ethylene-vinyl acetate/layered double hydroxide/graphite powder (EVA/LDH/GP) composites were fabricated. The results show that the as-prepared EVA/LDH/GP exhibits 81.1 and 54.2% reductions in the peak of the heat release rate (PHRR) and the average of the heat release rate (AHRR), respectively, relative to the neat EVA, indicating significantly improved flame retardancy. The combination of LDH and GP contributes to the formation of compact char layers due to their condensed-phase effect, thus leading to the significantly reduced heat release and improved fire safety of EVA composites. Such results further verify that waste-based RM can be used to prepare flame-retardant LDH because of its abundant metallic elements, for example, Al, Ca, and Fe. Fly ash rich in Si/Al oxides is also recognized as one class of effective waste flame retardants. reported the synthesis of stearic acid–modified fly ash and the preparation of the corresponding flame-retardant epoxy resins with various fly ash contents (see Figure 3). Twenty wt% of fly ash decreases the burning rate of epoxy thermoset to 16.78 mm/min and increases the LOI to 23.2% (see Figure 4), demonstrating the flame-retardant characteristic. In addition, employed magnesium alloy scrap to enhance the fire resistance of intumescent fire-retardant polyacrylate-based coatings applicable to structural steel. Magnesium alloy scrap is capable of significantly increasing the char expansion degree and suppressing the heat transfer of intumescent coatings when exposed to high-temperature flame (see Figure 5). In detail, introducing 0.48 wt% scrap reduces the backside temperature of the coating from 310 to 171°C by 44.8%, with a 100.8% increase in char expansion degree. The highly intumescent char effectively suppresses the heat transfer and protects the underlying steel during combustion. Hence, the waste-based magnesium alloy scrap can be used as a synergist for the intumescent fire-retardant systems that comprise ammonium polyphosphate (APP), pentaerythritol (PER), and melamine (MEL). Similar reuse of waste for the fabrication of fire-resistant polymers had also been reported by . Obviously, the flame-retardant element (e.g., Al, Mg, and Si)-rich industrial wastes can be applied in the preparation of flame-retardant polymeric materials. However, the compatibility between industrial wastes and polymeric materials is an unavoidable issue, which impacts the comprehensive properties of polymers, and thus significantly restricts the practical applications of industrial wastes. In addition, the efficiency of the industrial waste–based flame retardants is not high enough, and needs to be further increased.
FIGURE 1
FIGURE 2

Differential scanning calorimeter (DSC) curves of the neat ER and ER composites with different contents of ATFB, RM, and Al(OH)3 (
FIGURE 3

Schematic diagram of fly ash–containing epoxy networks after curing (
FIGURE 4

Fire resistance of epoxy resins containing fly ash or modified fly ash: (A) UL94 HB result, (B) combustion rate, and (C) LOI (
FIGURE 5

(A) Backside temperatures of coatings and (B) char expansion degrees of chars (
Domestic Waste
Domestic waste comprises disposable materials generated by households in daily activities. Nowadays, only some domestic waste can be recycled, and the rest will go to landfills. However, the landfills will be completely filled if the level of waste continues to grow rapidly. To help ease this issue, the reuse of domestic waste has been a high priority in recent years. Interestingly, many kinds of domestic wastes have been explored to create flame-retardant polymers. For example,
FIGURE 6

Illustration for (A) the preparation of CES bio-filler and (B) fabrication of CES-containing intumescent fire-retardant epoxy coatings (
FIGURE 7

Digital photographs of the epoxy coatings after LOI tests (
FIGURE 8

The fabrication of PA-B (
Plant Waste
There are two types of plant waste, cellulose nanofibers and lignin, that are often applied in the flame-retardant polymeric materials because of their renewable, biodegradable, and nontoxic characteristics (
FIGURE 9

Synthesis of P/N-containing lignin (Lig-M and Lig-F) (
FIGURE 10

(A) The design and preparation of both APP@CNF and its PLA composite, (B) Fourier transform infrared spectroscopy (FTIR) spectra of APP, CNF, and APP@CNF, and the weight–average particle size distribution of (C) 20% APP and (D) 10% APP@CNF in the PLA matrix (
FIGURE 11

(A) HRR and (B) mass loss curves of PLA biocomposites obtained from cone calorimeter tests with an external heat flux of 35 kW/m2 (
FIGURE 12

Synthesis of CP-lignin (
FIGURE 13

Scanning electron microscopy (SEM) images of the chars for PBS composites with (A, A′) 10 wt% CP-lignin, (B, B′) 20 wt% CP-lignin, and (C, C′) 30 wt% CP-lignin after cone calorimeter tests (
Conclusion and Perspectives
Recent years have witnessed the rapid development of waste-based flame retardants. Some industrial, domestic, and plant wastes have been applied in the fabrication of flame-retardant polymers because of their specific flame-retardant ingredients (see Table 1). However, the flame-retardant efficiency and compatibility issues of waste-based flame retardants have yet to be solved, thus restricting the practical applications of waste-based flame retardants. In the future, we should further increase the flame-retardant efficiency of waste-based flame retardants via the green method and prepare waste-based flame retardants with good compatibility for different polymers.
TABLE 1
| Waste type | Flame-retardant component | Other flame retardants | Polymer matrix | Flame retardancy and smoke suppression | References |
|---|---|---|---|---|---|
| Red mud | Fe/Al/Si elements | Al(OH)3 and ammonium tetrafluoroborate | Epoxy resin | The LOI reaches 29.0%. | |
| Fly ash | Si/Al oxides | / | Epoxy resin | The burning rate decreases to 16.78 mm/min, and the LOI increases to 23.2%. | |
| Magnesium alloy scrap | Mg/Al/Si oxides | APP, MEL, and PER | Polyacrylate | The backside temperature of the coated steel decreases to 171°C, and the char yield at 800°C reaches 27%. | |
| Chicken eggshell | Calcium carbonate | APP, MEL, and PER | Epoxy resin | The LOI reaches 31.5%, and the PHRR and TSR are decreased by 42.2 and 15.0%, respectively, in comparison to those of APP/PER/MEL-containing epoxy thermoset. | |
| Chicken eggshell | Calcium carbonate | APP and PER | Poly (lactic acid) | The LOI and UL-94 rating increase to 34.5% and V-0. | |
| Banana peel powder | Hydroxyls | Phytic acid | Poly (lactic acid) | The LOI and UL-94 rating increase to 37.5% and V-0. | |
| Bagasse | Hydroxyls | Chitosan, APP, and EG | Epoxy resin | The LOI and UL-94 rating increase to 25.8% and V-0, and the PHRR and TSR are decreased by 33.4 and 7.3%, respectively compared with those of bagasse-containing epoxy thermoset. | |
| Lignin | Hydroxyls | Piperazine and DOPO | Epoxy resin | The LOI and UL-94 rating increase to 34.3% and V-0, and THR and TSP are reduced by 46.6 and 53%, respectively. | |
| Cellulose nanofibers | Hydroxyls | APP | Poly (lactic acid) | The LOI and UL-94 rating increase to 32.5% and V-0, with 55.5 and 23.5% reductions in PHRR and THR, respectively. | |
| Lignin | Hydroxyls | Triazineand 2,6,7-trioxa-1-phosphabicyclo-[2,2,2]octane-4-methanol-1-oxide | Polybutylene succinate | The PHRR and THR are reduced by 27.2 and 31.1% compared with those of the neat polybutylene succinate. |
Flame retardancy and smoke suppression of the mentioned waste-containing polymers.
Statements
Author contributions
CG contributed to writing—original draft, review, and editing. SH contributed to conceptualization, writing—original draft, review, and editing. ZC contributed to investigation.
Funding
The authors gratefully acknowledge the financial support for this work by the Natural Scientific Foundation of Zhejiang Province (No. LY20E030001) and the Startup Foundation of Quzhou University (No. BSYJ202001).
Conflict of interest
Author ZC was employed by the company Ningbo Miruo Electronic Technology Co., Ltd.
The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
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Summary
Keywords
waste, sustainable development, polymeric materials, thermal stability, flame retardancy
Citation
Gao C, Huo S and Cao Z (2021) Solid Wastes Toward Flame Retardants for Polymeric Materials: A Review. Front. Mater. 8:712188. doi: 10.3389/fmats.2021.712188
Received
20 May 2021
Accepted
23 June 2021
Published
23 July 2021
Volume
8 - 2021
Edited by
Pingan Song, University of Southern Queensland, Australia
Reviewed by
Rongkun Jian, Fujian Normal University, China
Xiaming Feng, Louisiana State University, United States
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© 2021 Gao, Huo and Cao.
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*Correspondence: Siqi Huo, sqhuo@nbt.edu.cn
This article was submitted to Polymeric and Composite Materials, a section of the journal Frontiers in Materials
Disclaimer
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.