As a consequence of the rapid advancement of technology and the growth of the universal standard of living, public attention to environmental issues is on the rise [1–3]. Recent studies have demonstrated the presence of microplastics from the depths of the ocean (10,890 m) to the top of Mount Everest (8,840 m above sea level), which further exacerbates the prevailing concern regarding the environmental contamination of the planet [4–6]. In the contemporary era, the utilization of biodegradable plastics, including Poly (lactic acid) (PLA) [7–10], Poly butylene succinate (PBS) [11, 12], Poly (butylene adipate-co-terephthalate) (PBAT) [13], Polypropylene carbonate (PPC) [14, 15], and so forth, has emerged as a pivotal strategy to curb the reliance on petroleum-derived plastics and mitigate the detrimental effects of white pollution. Wherein, PLA is undoubtedly one of the most commercially valuable materials in the field of bioplastics, accounting for 18.9% of the market share of bioplastics [16], and has been applied in fields such as medical, packaging, agricultural and textile due to its excellent advantages in biocompatibility, biodegradability, and high transparency, but the inherent defects of PLA such as poor toughness, low thermostability, and high cost are significant factors limiting its broader use in industrial and commercial sectors [9, 17, 18]. By blending PLA with modifier, fillers or other biodegradable materials, products with desired properties can be obtained, which is a simple, effective, and highly cost competitive method [10, 19]. At present, for the purpose of realizing high-value utilization of waste and ensuring sustainable economic development, the use of waste resources as fillers in developing PLA-based composites has been widely studied [20–26]. Song et al. [22] used stannous octanoate as a catalyst to graft bamboo flour (BF) onto lactide (LA) in the molten state to form BF-g-LA, and then PLA is blended with BF (PLA/BF, 85/15 wt%) to prepare PLA/BF/BF-g-LA composites using BF-g-LA as a compatibilizer. It is found that the addition of BF-g-LA improved the interfacial compatibility between PLA and BF. When the amount of BF-g-LA is 2 phr, the tensile and impact strengths of PLA/BF/BF-g-LB composites are 55.3 MPa and 9.56 kJ/m, respectively, which are 30% and 27% higher than the corresponding values of PLA/BF composites.
Rice husk is a byproduct of the rice production process that is often disposed of through open burning, the practice that presents a significant challenge to the ecosystem, particularly in developing countries [27–29]. Green PLA composites manufactured using rice husk as a reinforcing material offer a novel technology that not only promotes environmental stewardship by reducing waste and carbon footprint, but also enhances prosperity by providing innovative economic opportunities for rice cultivation [30, 31]. However, PLA is a brittle material that is not easily processed, and the incorporation of rice husks has not resulted in a significant toughening effect [32]. In order to enhance the toughness of PLA/RH composites, it is necessary to add the ternary component, such as elastomers or small molecule plasticizers.
Acetyl tributyl citrate (ATBC) is a green and non-toxic citrate plasticizer, which has been approved as a plastic plasticizer for food packaging and medical devices [10, 33, 34, 35]. In this study we prepared a series of PLA/RH composites with ATBC by melt blending and hot compression with a rice husk amount controlled at 30%, exploring the effect of different amount of ATBC on composites characterized by Fourier transform infrared (FTIR) spectrometry, Mechanical properties, Thermogravimetric analysis (TGA), HAAKE torque rheometer, water absorption, contact angle, Dynamic mechanical analysis (DMA), Differential scanning calorimetry (DSC) and Scanning electron microscopy (SEM), which is able to give more excellent comprehensive performance composites.