Fig. 1: Scalable, continuous, and rapid preparation of high-performance paper plastic based on a transformative microwave radiation-driven dynamic carbamate chemistry. a Schematic demonstrating the preparation of the paper plastic. Firstly, the mixed solution of cyclic carbonate and PEI was compounded with cellulose paper, and then it was rapidly cured into paper plastic under microwave radiation. b Large-volume cyclic carbonates, PEI, and mixture solutions can be obtained. c A large-scale sheet of paper plastic. d Radar plots comparing the performance of paper plastic, cellulose paper, and polyethylene, in which the results are normalized by the maximum value of each characteristic. Source data are provided as a Source Data file.<\/p>\n Figure 2a<\/a> shows the design concept and possible reactions that the three initial reactants, CSBO, APAC, and PEI, would undergo during the preparation of paper plastics. A molar ratio of 1:1 between the cyclic carbonate groups (from CSBO and APAC) and the amino groups (from PEI) is employed to theoretically ensure the complete reaction of these functional groups to form carbamate dynamic bonds that are highly attractive for mechanical strength and bond exchangeability. To ascertain the proposed reaction route, a combined spectrum investigation was performed on the reactants, intermediates, and products. Comparing the FTIR spectrum of the obtained paper plastic with those of the reactants (Fig. 2b<\/a>), it is seen that the absorption peak (1797\u2009cm\u22121) assigned to cyclic carbonate significantly weakens after the reaction, associated with the appearance of an absorption peak (1690\u2009cm\u22121) belonging to C=O of the carbamate bond. Meanwhile, the two absorption peaks in 3300\u20133500\u2009cm\u22121 belonging to \u2013NH2 of PEI disappeared. Collectively, the peak intensity evolution of these characteristic functional groups confirmed the synthesis route of NIPU. Moreover, original cellulose paper possesses a porous structure, which can facilitate the rapid penetration of the reactant mixture before curing. Consequently, the inter-fiber pores are completely and homogeneously filled during the curing process, as demonstrated by combined morphological and compositional analyses through the surface and cross-sectional SEM observation and the corresponding EDS elemental mapping images (N element exclusively attributable to NIPU) of the original cellulose paper and the as-prepared paper plastic (Fig. 2c<\/a> and Supplementary Fig. 8<\/a>). Subsequently, Raman and FTIR of cellulose and the cellulose plastic were performed to explore the carbamate bonding chemistry after the introduction of NIPU.<\/p>\n Fig. 2: Morphological and structural features of paper plastic. a Schematic of polymer (NIPU) preparation. b FTIR spectra of CSBO, APAC, PEI, and NIPU. c SEM images of cellulose paper and paper plastic. Scale bar, 50\u2009\u03bcm. d One-dimensional Raman spectra and two-dimensional (2D) Raman spectra constructed from the intensity of C=O. e FTIR spectra of paper and paper plastic. Source data are provided as a Source Data file.<\/p>\n Comparing the Raman spectra of the cellulose paper40<\/a> and the paper plastic, the absorption peak of C=O of carbamate is found at ~1600\u2009cm\u20131 with the incorporation of NIPU (Fig. 2d<\/a>). The corresponding 2D Raman mapping (with an area of 200\u2009\u00d7\u2009200\u2009\u03bcm2, red color represents a higher absorption intensity) further indicates the high abundance and uniform distribution of carbamate bonds across the paper plastic surface. In the FTIR spectrum of paper plastic (Fig. 2e<\/a>), a typical carbonyl peak appears at 1740\u2009cm\u22121, accompanied by a \u2013NH\u2013 bending vibration peak at 1550\u2009cm\u22121 corresponding to the free carbamate groups of the introduced polymer41<\/a>. The formation of these groups occurs through the reaction between the amine groups and the cyclic carbonates. Furthermore, the presence of hydrogen bonds between carbamate groups or between carbamate groups and hydroxyl groups leads to the emergence of new absorption peaks in the range 1715\u2009\u2212\u20091695\u2009cm\u22121 for the paper plastic, compared with that of the cellulose paper. The dynamic covalent bond can further undergo exchange reaction with \u2013OH in cellulose paper (Fig. 2c<\/a>), thus achieving efficient cross-linkage between NIPU and the cellulose substrate.<\/p>\n Additionally, we believe that during the microwaving-induced polymerization process, the carbamate moiety of NIPU would suffer from C\u2013O bond cleavage and rearrangement reaction with the hydroxyl groups on the cellulose chain, based on the solid-state 13C NMR results (Supplementary Fig. 10<\/a>): in addition to the new peak at 153.7 ppm attribute to the carbamate group42<\/a>, the peak shift of C1 (107.3 ppm) and C4 (90.8 ppm) of cellulose43<\/a> to the high field and a significant shoulder peak of C6 (65.4 ppm) were observed, which is attributed to the cross-linking between the C6\u2013OH and NIPU. Consistently, theoretical calculation reveals that the formation of carbamate connection between NIPU and cellulose is thermodynamically favorable with a high binding energy (Supplementary Table 2<\/a>).<\/p>\n Mechanistic insights into the strengthening mechanism of paper plastic<\/p>\n The mechanical properties of common cellulose paper are not competitive enough compared to plastic materials. Moreover, cellulose paper is more prone to breakage upon moisture exposure or being wetted due to the sharp decrease of contact areas between cellulose fibers and hence the number of hydrogen bonds in these areas. As shown in the tensile strain\u2013stress curve, the cellulose paper used in this work shows a fracture strength of 13\u2009MPa, with the incorporation of NIPU, a drastic improvement, by a factor of ~10, to 126\u2009MPa was observed for the paper plastic (Fig. 3a<\/a>). Concurrently, 2.5 and 24 times increase of the Young\u2019s modulus and toughness compared to the cellulose paper were also achieved (Fig. 3b<\/a>). In a more visual demonstration of such exceptional mechanical properties of the as-prepared paper plastic, a paper plastic sample measuring 100\u2009mm (width)\u2009\u00d7\u20090.36\u2009mm (thickness) was shown to support an adult weighing 65\u2009kg (Supplementary Fig. 13<\/a>). The combination of these mechanical properties makes the paper plastic a promising alternative to numerous natural and synthetic materials (Fig. 3c<\/a>). Considering the low tensile strength of only ~3.2\u2009MPa for NIPU, it is reasoned that the reformation of hydrogen bonds37<\/a> and carbamate linkages between cellulose and NIPU is responsible for the significant interfacial reinforcement and therefore the mechanical properties.<\/p>\n Fig. 3: Enhanced mechanical properties and mechanistic insights into the strengthening mechanism of paper plastic. a Stress\u2013strain curves of the cellulose paper and paper plastic. b Comparison of Young\u2019s modulus, tensile strength, and toughness of paper (Young\u2019s modulus: 1\u2009GPa, strength: 13\u2009MPa, toughness: 0.15\u2009MJ\/m3) and paper plastic (Young\u2019s modulus: 3\u2009GPa strength: 126\u2009MPa, toughness: 3.63\u2009MJ\/m3). Values in b represent their means\u2009\u00b1\u2009SDs from n (number of the repeated experiment)\u2009=\u20093 independent samples. c Ashby diagram of tensile strength vs. Young\u2019s modulus for paper plastic compared with typical polymers. d Color-coded two-dimensional maps of stresses carried by cellulose paper at a strain of 5%. e Color-coded two-dimensional maps of stresses carried by paper plastic at a strain of 5%. f SEM image and simulated fracture surface features of the paper. Scale bar, 500\u2009\u03bcm. g SEM image and simulated fracture surface features of paper plastic. Scale bar, 500\u2009\u03bcm. Source data are provided as a Source Data file.<\/p>\n To understand the microstructural evolution and performance improvement in paper plastic, we constructed multiscale simulations and analyses for the paper plastic based on experimental evidence (see Supplementary Information for details). The simulated strain\u2013stress curves exhibit good agreement with the experimental measurements. The simulated stresses corresponding to the experimental failure strains for cellulose paper and paper plastics are 12 and 156\u2009MPa, respectively, which align with the experimental values (13 and 126\u2009MPa, respectively). To demonstrate the decisive role of carbamate linkage between cellulose and NIPU in boosting the mechanical performance, an elastic silicone rubber (SR) that shows very similar mechanical behavior (rubber-like) and tensile strength (~3\u2009MPa for NIPU vs. 1.38\u2009MPa for SR) with NIPU, and meanwhile is unlikely to form covalent cross-linking, was synthesized to serve as a control in this study. As the morphological, compositional, and mechanical analyses reveal, although the cellulose paper can also be homogeneously and fully filled the SR, a tensile strength of only 21\u2009MPa was measured (Supplementary Figs. 15<\/a>, 16<\/a>). This indirectly but strongly suggests that chemical cross-linking between cellulose and NIPU did occur within the paper plastic. Furthermore, the microstructural evolutions of microfibrils in cellulose paper and paper plastic under uniaxial tension were analyzed. Upon a certain stretching, the stress levels of paper plastic are significantly higher than cellulose paper (Fig. 3d<\/a>, e and Supplementary Figs. 17<\/a>\u201319<\/a>), which is attributed to that the carbamate linkage improves stress transfer efficiency. Our simulations show that the existence of a carbamate linkage can significantly impede the slippage of microfibrils, thus enabling exceptional mechanical properties of the paper plastic. These simulations are also supported by the experimental observations, for example, both SEM images and simulations show that a flat fracture surface is retained for the paper plastic (Fig. 3<\/a>f, g<\/a> and Supplementary Fig. 20<\/a>), while the cellulose paper shows a messy fracture surface due to the slippage of cellulose microfibrils.<\/p>\n Considering the feasibility and high efficiency of this dynamic carbamate chemistry approach, it is theoretically applied to various types of daily-used paper products with cellulose materials as the primary component. Using the same process parameters, paper plastics based on a wide spectrum of cellulose paper products including hardwood pulp paper (HPP), softwood pulp paper (SPP), filter paper (FP), kraft paper (KP), printer paper (PP), tissue paper (TP), and newspaper (NP) were prepared with their digital photographs shown in Supplementary Fig. 21<\/a>. The tensile stress\u2013strain results reveal that after compounding with NIPU the mechanical properties of all cellulose papers can be significantly improved by almost one order of magnitude (Supplementary Fig. 22<\/a>). Taking HPP, SPP, and SPP as examples, their tensile strengths are determined to be 72.95, 94.26, and 103.16\u2009MPa, respectively, to list a few. These results substantiate the applicability and generality of the preparation method for high-performance paper plastics.<\/p>\n Other required properties for plastic substitution applications<\/p>\n Conventional plastic materials are usually hard to operate under extreme temperature environments due to their insufficient thermal dimensional stability4<\/a>,44<\/a>. The limitation is well addressed for our paper plastics, mainly benefiting from the excellent thermal (dimensional) stability of the cellulose paper, thereby making them more competitive in plastic substitution. Quantitatively, according to the coefficient of thermal expansion (CTE) test results\u00a0(Fig. 4a<\/a>), the paper plastic exhibits a rather low CTE value of 3.54\u2009\u00b5m\/(m\u00b7\u00b0C) (determined in the temperature range 0\u2212100\u2009\u00b0C), significantly lower than widely used commercial plastics (PP, PE, PS, and PLA). More intuitively, commercial plastics exhibit softening and shrinkage when placed on a hot plate at 150\u2009\u00b0C for 20\u2009min, whereas the paper plastics have no visible changes (Fig. 4b<\/a>). For better comparison with commercial plastics, we have also supplemented the thermal expansion test results of epoxy and polyurethane (PU) (Supplementary Fig. 23<\/a>). These results show that paper plastics can exhibit thermal stability similar to thermosetting epoxy resins, and further prove that paper plastics have well thermal stability. In addition, TGA testing showed that the initial weight loss temperature (T5%) of paper plastic exceeded 250\u2009\u00b0C (Supplementary Fig. 24<\/a>), indicating the excellent thermal stability of the paper plastic. The TG\u2013FTIR test also confirmed the significantly suppressed thermal decomposition process of the paper plastic, as shown in Supplementary Fig. 25<\/a>.<\/p>\n Fig. 4: Thermal, water, and solvent stability of paper plastic. a Coefficient of thermal expansion (CTE) and thermal expansion of polypropylene (PP), polyethylene (PE), polystyrene (PS), poly(lactic acid) (PLA), and paper plastic. b Thermal stability experiment. Comparison of the paper plastic with widely used petroleum-based plastics at 27\u2009\u00b0C (RT) and 150\u2009\u00b0C. Compared to 27\u2009\u00b0C, petroleum-based plastics have already fully softened and deformed at 150\u2009\u00b0C, while paper plastic still shows no visible change. c Water uptake of cellulose paper, NIPU, and paper plastic. The error bars represent the standard errors from three samples for each material. The insets are photographs for water contact angle measurement for the cellulose paper and paper plastic samples. d Tensile strain\u2013stress curves of cellulose paper and paper plastic after soaking in water for 7\u2009d. The inset shows the measured tensile strength with error bars representing the \u00b1SDs (number of the repeated experiment\u2009=\u20093). e Stability of paper plastic in organic solvents after 7\u2009d. Source data are provided as a Source Data file.<\/p>\n The hydrophilicity of cellulose often leads to inadequate water resistance for paper packaging materials45<\/a>,46<\/a>, necessitating the urgent need for addressing this issue and enhancing their water resistance. By incorporating NIPU with hydrophobic aliphatic chains to encapsulate the hydrophilic cellulose paper fibers, the paper plastics exhibit satisfactory waterproof ability. The NIPU-coated paper exhibits a water contact angle of over 100\u00b0 (Fig. 4c<\/a>), demonstrating significant hydrophobicity compared to unmodified paper (almost no contact angle). Taking into account the influence of hydroxyl groups in the paper plastic, we supplemented the evolution of the contact angle over time. As shown in Supplementary Fig. 26b<\/a>, the contact angle of the paper plastic surface hardly changes as the time extends from 0 to 120\u2009min, and remains at about 100\u00b0, which indicates that the stable hydrophobicity and suggests that the crosslinked NIPU network effectively restricts water penetration. Moreover, cellulose paper and paper plastics are immersed in water for 7 days, and their water absorption is recorded. Figure 4c<\/a> shows that cellulose paper exhibits 160% water absorption, while paper plastic absorbs only 20%. The wet tensile strength of the paper plastic can be maintained at ~89\u2009MPa (about 72% of the dry paper plastic) after soaking for one week\u00a0(Fig. 4d<\/a>). These results indicated that the incorporation of NIPU into the cellulose paper network effectively enhances the mechanical properties of paper plastic in wet environments. Importantly, this hydrophobicity is achieved while maintaining high biobased content (82%) and full recyclability, which represents a key advance over conventional petroleum-based plastic coatings. Furthermore, Paper plastics were immersed in various organic solvents (MeOH, EtOH, IPA, acetone, EtOAc, THF, DMF, hexane, and toluene) to study their solvent resistance (Fig. 4e<\/a>). After 7-day immersion, no noticeable color and size change for the paper plastic was observed (Supplementary Fig. 26c<\/a>), showing excellent solvent resistance across a wide variety of common solvents.<\/p>\n From raw materials to products<\/p>\n Because the dynamic carbamate linkage can break and reform with moderate energy input, paper plastic components can readily be bonded together to prepare various products. In a simple attempt, single-layer paper plastics were effectively combined through hot pressing to obtain high-strength boards (Fig. 5a<\/a>). SEM image analysis (Supplementary Fig. 27a<\/a>) reveals a closely stacked cross-section architecture of the multi-layer paper plastic after hot pressing. Supplementary Fig. 28a<\/a> demonstrates the load-bearing capacity of the paper plastic board. Figure 5b<\/a> shows that the edges of the paper plastics can be hot pressed to realize heat-sealing through the dynamic bond exchange reaction for the demonstration of daily packing bags (see Supplementary Fig. 29<\/a> for more details). To examine the adhesion limit, two rectangular paper plastics were subjected to a tensile test on a universal testing machine after being welded by hot pressing to verify their heat-sealing ability. It is evident that the paper plastic fractures during the test, while the welded position remains intact (Supplementary Fig. 30<\/a>), which demonstrates its excellent heat-sealing ability for adhesive-free packaging products. Given the excellent water resistance of the paper plastic, cups and straws were produced and tested, with commercial products as the control group, unexpectedly, only the paper plastic group exhibits persistent wet strength, allowing continuous use in various aqueous environments for over 6\u2009h (Supplementary Fig. 31<\/a>).<\/p>\n Fig. 5: Production of various paper plastic products with excellent comprehensive performances. a Schematic illustration showing the preparation process\u00a0of thick\u00a0paperboard from multiple thin paper plastic sheets\u00a0by hot pressing and the photographs\u00a0of multiple paper plastic boards. b Schematic illustration of the plastic bag preparation process using paper plastic. A large number of bags are made of paper plastic. c Compression stress\u2013strain curve of paperboard. d Comparison of Charpy impact toughness of paper plastic with other widely used polymer-based materials. e The oxygen transmission rate of different plastics and paper plastic at 23\u2009\u00b0C\/90% RH. HDPE high density polyethylene, PP polypropylene, PET polyethylene terephthalate, PVC polyvinyl chloride, PA polyamide, PC polycarbonate, ABS acrylonitrile butadiene styrene. f In vitro cytotoxicity test of paper plastic, including cell morphology and cell viability ratios of 25, 50, 75, and 100% sample extracts. Error bars in d, e, f indicate \u00b1 SDs from three measurements. g Skin irritation test of paper plastic. h Skin sensitization test of paper plastic. Source data are provided as a Source Data file.<\/p>\n Compression and Charpy pendulum tests were performed47<\/a> to demonstrate the mechanical properties of the paper plastic board. The compressive strength of a paper plastic board is 96.5\u2009MPa (Fig. 5c<\/a>), while its impact toughness measures 170.6\u2009kJ\/m2 (Fig. 5d<\/a>), surpassing that of a considerable number of commercial plastics. These results suggest that the paper plastic possesses good thermal lamina ability due to the presence of dynamic covalent bonds, thereby enabling its application as building blocks of composite board. Additionally, the paper plastics can be easily imbued with oily dyes (Supplementary Fig. 32<\/a>), thereby augmenting the chromatic diversity. The gas barrier is also an important property of packaging materials48<\/a>. Figure 5e<\/a> and Supplementary Fig. 33a<\/a> demonstrate significantly lower oxygen transmission rate (OTR, 72\u2009cm3\/(m2\u00b724\u2009h\u00b70.1\u2009MPa)) and nitrogen transmission rate (NTR, 25\u2009cm3\/(m2\u00b724\u2009h\u00b70.1\u2009MPa)) for paper plastic compared to cellulose paper alone. The reason is that NIPU can penetrate the original pores between the paper fibers, blocking the passage of gas in the cellulose paper. Additionally, the formation of a NIPU film on the surface of hydrophilic paper fiber further hinders gas diffusion. Moreover, the paper plastic shows desirable gas barrier (indicated by oxygen transmission rate) comparable and modest moisture barrier (indicated by water vapor transmission rate) abilities compared to commercial plastics49<\/a>, further validating its application potential as packaging materials (Supplementary Fig. 33b<\/a>).<\/p>\n Biocompatibility analysis of paper plastic<\/p>\n To further broaden the application properties of paper plastics, biocompatibility experiments were carried out, including in vitro cytotoxicity test, skin irritation test, and skin sensitization test. After cultured with paper plastic extract and L-929 cells for 24\u2009h, the cell morphology was observed, and the cell viability ratio was quantified by the MTT method. As shown in Fig. 5f<\/a> and Supplementary Fig. 34<\/a>, the cell viability ratios of 25, 50, 75, and 100% sample extracts were all higher than 80%, while maintaining predominantly intact cellular morphology. These results confirm that the paper plastic has less cytotoxicity to L-929 cells and meets the acceptance standard according to the national standard ISO10993\u20135: 2009. In addition, skin irritation and sensitization tests are also carried out as the materials will direct contact with human skin. Following the ISO10993\u201310: 2010 standard, paper plastic was extracted with 0.9% NaCl injection (polar extract) and sesame oil (non-polar extract). Then, gauzes moistened with the extracts were applied to the back of the New Zealand rabbit for a skin irritation experiment, which were removed after 4\u2009h. The animals were observed at 24, 48, and 72\u2009h after the gauze was removed. Figure 5g<\/a> illustrates no presence of erythema or edema on the skin surface. Meanwhile, based on the classification system of skin reactions (Supplementary Tables 3<\/a>, 4<\/a>), all experimental rabbits exhibited a primary irritation index of 0 when exposed to paper plastic (Supplementary Table 5<\/a>), indicating its non-inductive nature towards skin irritation. The skin sensitization test was conducted using the guinea pig maximization test (ISO10993\u201310: 2010 standard, Fig. 5h<\/a>). Firstly, the extract was injected into the medial scapula of guinea pigs for intradermal induction, and then the gauzes wetted by the extract was applied to the injection site of the animal for 48\u2009h to experience topical induction after 7 days. After 15 days, the gauzes wetted by the extract were applied to the left and right abdomen of guinea pigs for 24\u2009h to challenge. The appearance of the injured part of the animal was observed 24 and 48\u2009h after the removal of the dressing, revealing no signs of erythema and edema (Fig. 5h<\/a>). Moreover, according to the Magnusson and Kligman scale provided in Supplementary Table 6<\/a>, paper plastic exhibited a sensitization grade score of 0, indicating a sensitization positive rate of paper plastic at 0%. Concurrently, positive control and negative control experiments were conducted on experimental animals to confirm the effectiveness of paper plastic skin irritation and sensitization tests.<\/p>\n Environmental impacts of paper plastic<\/p>\n Cellulose paper is a highly biodegradable material. Therefore, it is desirable to retain its inherent ability to degrade easily even after modification. To this end, the cellulose paper, paper plastic, NIPU, and commercial plastics (polyethylene (PE)) were buried in a natural environment (Nanjing, China) for performing biodegradability tests (Fig. 6a<\/a> and Supplementary Fig. 35<\/a>). The NIPU was introduced into the cellulose paper is derived from biobased raw materials (APAC and CSBO) and biodegradable PEI50<\/a>, enabling the paper plastic to undergo decomposition by microorganisms and participate in the cycle of the ecological environment after being buried in the soil. Similar to the rapid degradation of cellulose paper observed in soil, the paper plastic exhibited initial signs of degradation after being buried in the soil for 1 month, as evidenced by the presence of holes on its surface, which could be attributed to microbial activity and enzymatic action in the soil23<\/a>,51<\/a>. Subsequently, an increase in microbial content on the material surface facilitated the hydrolysis of hydrogen bonds and chemical bonds27<\/a> in the paper plastic, which promoted the complete degradation of the paper plastic within 180 days. Meanwhile, noticeable degradation of NIPU was observed at 210 days. In contrast, the commercial PE buried in the soil exhibits no changes and may require several decades to centuries for degradation. Paper plastics can maintain stability under normal working conditions but undergo degradation when buried in soil, highlighting their exceptional biodegradability. In addition, data on the amount of CO2 produced by microorganisms during the biodegradability process (Supplementary Fig. 36<\/a>) and the possibility of microplastics being produced (Supplementary Fig. 37<\/a>) after the degradation of paper plastics are measured. The results confirm that the paper plastics are biodegraded during the degradation process, and there is no obvious production of microplastics. This characteristic renders it a promising alternative to conventional plastic packaging materials.<\/p>\n Fig. 6: Environmental impacts of paper plastic. a Degradation process of paper plastic, and polyethylene (PE) buried in soil (Nanjing). b Physical recyclability of paper plastics. Shredded paper plastic recovered to intact paper plastic after hot pressing and cross-section SEM image of the reprocessed paper plastic. Scale bar, 200 \u03bcm. c Chemical recyclability of paper plastics. Photos show the degradation of paper plastic in 0.5\u2009M NaOH solution and the regeneration of cellulose paper from recyclables. d Cradle-to-grave climate change potential (normalized to tensile strength) of the paper plastic compared to 14 potentially competitive benchmark plastic films and composite materials using life cycle assessment (LCA). e Comparison of the economic cost of paper plastic to commercial plastics (PE, PET, PP, PLA, and PCL) via TEA. PP polypropylene, LDPE low density polyethylene, PB polybutylene, PU polyurethane, PLA polylactic acid, PVF poly(vinyl formal), PVDC polyvinylidene chloride, PMMA poly(methyl methacrylate), PA\/GF polyamide\/ fiberglass, ABS\/CF acrylonitrile butadiene styrene\/carbon fiber, PCL polycaprolactone, PE polyethylene. Source data are provided as a Source Data file.<\/p>\n Due to the dynamic carbamate bond constructed in paper plastics, they can also be recycled in addition to experience biodegradation, which challenges the problem of traditional plastics that are difficult to degrade and effectively alleviates the environmental problems. The carbamate groups containing \u03b2\u2013OH formed after introducing NIPU into the cellulose paper can undergo a bond exchange reaction with the hydroxyl groups. This enables the rearrangement of the network structure and facilitates the reprocessing of paper plastics. As shown in Fig. 6b<\/a>, the fragmented paper plastic can become a complete material after hot pressing. However, due to the presence of non-malleable cellulose paper components comprising 50% of the recycled content, discernible surface textures are observed on the reprocessed paper plastic. Nevertheless, as evidenced by the SEM image of the cross-section, the re-cross-linking process has successfully taken place. Moreover, Fig. 6c<\/a> shows the chemical recyclability of paper plastics. The carbamate bonds in the paper plastics readily undergo alkaline hydrolysis when exposed to boiling NaOH solution, resulting in the depolymerization of NIPU into smaller molecules and separation from the cellulose paper substrate. The cellulose paper fibers can be easily collected for recycling through filtration and subsequently reconstituted into a complete piece of paper after the papermaking process. This straightforward approach demonstrates a simple yet effective method for achieving the recycling of paper plastics. Moreover, the recovery experiments of the pure polymer in the paper plastic (NIPU) were provided to demonstrate dynamic carbamate chemistry more clearly (Supplementary Fig. 38<\/a>). The re-curing NIPUs obtained by physical hot pressing and chemical degradation confirm the dynamic properties of the network structure.<\/p>\n Life cycle assessment (LCA) was applied to determine the cradle-to-grave environmental impacts of paper plastic, i.e., from resource extraction to end-of-life (EoL). The climate change potential is used to understand the environmental sustainability of the material because it quantifies the greenhouse gas emissions driving climate change, a major global challenge nowadays. Besides, it also provides a common reference for comparing with other products or processes. The climate change potential (normalized to tensile strength as done by ref. 6<\/a>) in Fig. 6d<\/a> shows a significantly lower value for paper plastic over 14 potentially competitive benchmark plastic films and composite materials. Such a notably low carbon footprint originates from the manufacturing process simplicity, significant biogenic carbon content, and high strength of the paper plastic. As shown in Supplementary Fig. 39<\/a>, the manufacturing of paper plastic (cradle-to-gate) presents a carbon footprint of 6.81\u2009kg CO2 equiv kg\u22121, which is just under average for conventional plastics and composites. As a matter of fact, the obtained footprint value is just slightly above the cradle-to-gate carbon footprint of 2.6 and 2.9\u2009kg CO2 equiv kg\u22121 of HDPE and LDPE52<\/a>, or the ~4.75\u2009kg CO2 equiv kg\u22121 reported by ref. 53<\/a> for non-isocyanate poly-thiourethane production (no biogenic credits), a sustainable alternative to conventional plastics. However, it should be noted that the obtained footprint represents a conservative value, as the PEI modeled has a carbon footprint of 21.74 (lower values are more likely for industrially processed PEI). Furthermore, the biodegradability and large biogenic content of the paper plastic are translated into reduced CO2 emission at the EoL. The incineration of conventional plastics and composite materials is subjected to additional burdens because the additional energy input for burning plastics, as well as for the CO2 emissions originating from the fossil carbon that remains in the plastics (this adds approximately 6\u2009kg CO2 equiv kg\u22121). On the contrary, materials from biobased feedstocks can be composted and the CO2 formed during aerobic composting can be accounted as burden free because it will be included in the short-term carbon cycle again54<\/a>. The footprint per kilogram of final material is therefore lower, which together with its good mechanical properties makes paper plastic a low carbon material when the tensile strength is taken as a functional unit (as shown in Fig. 6d<\/a>). As shown in Supplementary Fig. 40<\/a>, the environmental impact of paper plastic is primarily attributed to PEI, which contributes 11.5 to 54.6% of the impact, ranking first in 13 out of the 16 environmental impact categories. Cellulose paper, soybean oil and acrylpimaric acid are the other major contributors, especially in the categories of land use, marine eutrophication and non-carcinogenic human toxicity, respectively. Unlike other studies, the energy consumption in paper plastic production is very low, with a maximum contribution of 0.1%.<\/p>\n![\"figure](\"https:\/\/www.newsbeep.com\/au\/wp-content\/uploads\/2025\/07\/41467_2025_61722_Fig1_HTML.png\")
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