Open Access Article
Hangtian Hu,
Wenping Li*,
Hui Zheng,
Zheng Li,
Aiguo Wang,
Zhangxin Chen and
Jinguang Hu
*
Department of Chemical and Petroleum Engineering, University of Calgary, 2500 University Drive, NW, Calgary, Alberta T2N 1N4, Canada. E-mail: wenping.li@ucalgary.ca; jinguang.hu@ucalgary.ca
First published on 7th April 2026
Sustainable ammonia (NH3) synthesis under moderate conditions, powered by renewable electricity and with reduced CO2 emissions, is a promising alternative to the energy-intensive Haber–Bosch process. In this work, we developed a non-thermal plasma (NTP) process that simultaneously realizes the synthesis of NH3 and the upcycling of high-density polyethylene (HDPE) waste with N2, H2O, and HDPE as feedstocks. A pronounced synergistic effect on NH3 yield was observed when HDPE was introduced. HDPE not only acted as a hydrogen donor but also as an oxygen scavenger to suppress H/O recombination, which led to an NH3 yield increase from 0.7 to 55.9 μmol h−1 under low N2 flow rate conditions, a 78.9-fold increase relative to the case without HDPE. This study offers a novel route for integrating low-carbon NH3 synthesis with plastic waste valorization, contributing to sustainable energy and waste management strategies.
Green foundation1. This work demonstrates the potential of waste plastics as an additional hydrogen donor in plasma-assisted ammonia synthesis from N2 and H2O, enabling high-yield NH3 production while simultaneously upgrading waste plastics under ambient conditions. This route offers a potential alternative to the conventional Haber–Bosch process by avoiding external H2 supply and high-temperature/high-pressure operation.2. Using high-density polyethylene (HDPE) as a model plastic, packing HDPE substantially enhanced NH3 formation, increasing the production rate from 0.7 to 55.9 μmol h−1 (a 78.9-fold increase). Simultaneously, value-added gaseous byproducts derived from HDPE decomposition, including H2, CO, CH4, and C2H6, were generated steadily. 3. Future work will optimize reactor design and plastic packing modes to increase productivity and enable scale-up at lower specific energy input. Incorporating catalysts will further direct plastic conversion toward targeted products and improve NH3 selectivity and energy efficiency. |
Given that conventional H2 production is generally from fossil fuels, replacing the fossil fuel with H2O as the hydrogen source offers a promising pathway to mitigate carbon emissions. Nowadays, the application of electrocatalytic and photocatalytic methods in the nitrogen reduction reaction (2N2 + 6H2O → 4NH3 + 3O2) has been widely investigated.7–9 However, the NH3 yield is limited due to the high bond energy of the N
N bond (941 kJ mol−1), poor N2 solubility, and low N2 diffusion coefficient in aqueous solvents. To tackle these issues, non-thermal plasma (NTP) technology has posed a possible solution, which can generate high-energy electrons to activate inert N2 into more reactive, vibrationally or electronically excited states under mild conditions, facilitating the cleavage of the N
N bond.10,11 Dielectric barrier discharge (DBD) plasma, as one of the NTP technologies, is extensively investigated among NTP technologies because of its ability to incorporate catalysts or other materials within the reactor while preventing arc discharges from causing damage.
So far, two types of experimental setups have been reported, distinguished by whether H2O is introduced into the plasma discharge zone. One is a plasma–liquid interface system for NH3 synthesis developed by Haruyama's group,12,13 in which N2 is activated by plasma discharge and subsequently transported to a separate chamber to react with H2O at the interface. The other is introducing H2O directly into the discharge zone, enabling a one-step reaction with N2 to produce NH3. Toth et al.14 developed a continuous ammonia generation system by co-feeding N2 gas and atomized H2O droplets into a DBD reactor, achieving an NH3 yield of 11 ± 1 μmol h−1. However, a current challenge of H2O as the hydrogen donor for ammonia synthesis is the low density of generated H species, which tend to recombine with O species, resulting in low energy efficiency and low NH3 yield.
In parallel, plastic waste upcycling has emerged as an urgent and rapidly growing research direction, driven by the massive accumulation of waste polymers and the need to convert them into value-added chemicals and fuels.15 In particular, global annual plastic production has increased from about 2 million metric tons (Mt) in 1950 to roughly 400 Mt by 2022.16 Recently, NTP has also been explored as a promising platform for plastic waste upcycling to hydrogen. For example, Trelles's group17 developed ambient-pressure reactors based on transferred-arc and gliding-arc discharges to convert low-density polyethylene (LDPE) into hydrogen, achieving maximum H2 productions of 0.33 and 0.42 mmol g−1 LDPE, respectively.
In this work, to overcome the intrinsic limitation of H2O-based plasma for ammonia synthesis and boost the ammonia yield, we creatively introduced plastic waste into the DBD reactor, by providing a second hydrogen donor and consuming oxygen generated from H2O decomposition to generate more H species. In this novel process, NH3 synthesis can be concurrently coupled with plastic waste valorization within a single reactor. High-density polyethylene (HDPE) was selected as the model plastic to realize and explore this plastic-boosted ammonia synthesis process, owing to its large market share, high hydrogen content (high H/C ratio), and the absence of oxygen in its polymer backbone. Control experiments were conducted to elucidate the effects of HDPE packing amount, H2O concentration, flow rate, and specific energy input (SEI) on the yields of NH3 and gaseous products. Based on product analysis and characterization of fresh and spent HDPE, a plausible reaction mechanism was proposed.
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| Fig. 1 Schematic of the experimental setup for plasma-assisted NH3 synthesis from N2, H2O and plastic waste. | ||
The influence of H2O concentration on NH3 synthesis was further investigated through control experiments. As depicted in Fig. 2d and Fig. S7, increasing the H2O concentration from 0 to 2.64 mol% (H2O saturation percentage from 0 to 100%) improved the NH3 yield from 34.3 to 55.9 μmol h−1 and the H2 yield from 810.6 to 1280.7 μmol h−1, demonstrating that H2O also served as an effective hydrogen donor for NH3 and H2 formation when HDPE was packed. In addition, increasing the H2O concentration revealed a clear synergy between H2O dissociation and HDPE decomposition to H species. In the absence of HDPE packing, the H2 yield remained relatively low (Fig. 2c), only 21.2 μmol h−1, indicating weak H2O dissociation. By contrast, under HDPE packing conditions, raising the H2O concentration substantially increased the H2 yield (Fig. S7), suggesting that the presence of HDPE promotes H2O activation and amplifies the H2O concentration dependence of H2 production. This enhanced dissociation implies that HDPE could function as an oxygen scavenger, capturing oxygen atoms liberated during H2O cleavage (verified further below) and thereby preventing H/O recombination. Furthermore, the presence of H2O in the DBD reactor led to the formation of CO and NOx gases. CO is formed via coupling between carbonaceous fragments from HDPE and oxygen species from H2O dissociation under plasma discharge, whereas NOx arises from oxidation of nitrogen-centered radicals formed during the reaction. NOx was captured in two tandem sulfuric acid bottles, yielding aqueous nitrate and nitrite. Both the CO yield and the combined nitrate/nitrite yields increased monotonically with H2O concentration (Fig. S7 and S8). Limited CO2 was generated upon H2O introduction, with the yield increasing from 0 to 21.0 μmol h−1 as the H2O concentration rose from 0 to 2.64 mol%. Temperature monitoring of the discharge region further showed that, under the same input power, the measured discharge region temperatures were essentially identical for the empty-tube and HDPE-packed reactors, and no obvious difference in the discharge region temperature was observed within the investigated range with varying H2O content or HDPE packing amount (Fig. S9).
The influence of N2 flow rate and SEI on NH3 production was systematically investigated, with SEI controlled via input voltage adjustment. As shown in Fig. 3a, increasing the N2 flow rate enhanced NH3 yields in both empty and HDPE packing reactors. This trend is attributed to the reduced gas residence time at higher flow rates, which mitigates equilibrium constraints on NH3 formation by suppressing its reverse dissociation.21 At 10 SCCM, HDPE packing increased the NH3 yield from 0.7 to 55.9 μmol h−1, representing a pronounced 78.9-fold enhancement, while the energy efficiency increased from 0.30 to 23.76 mg kWh−1. Even at 1000 SCCM (GHSV ≈ 20
000 h−1), HDPE packing still delivered a 3.7-fold increase, increasing the NH3 yield from 26.2 to 92.3 μmol h−1 and the energy efficiency from 11.1 to 39.2 mg kWh−1. The weakened HDPE packing benefit at high gas flow rates is attributed to the dilution effect of high flow rates, where the residence time shortens and reactive H species are diluted and swept out more rapidly, thereby weakening HDPE's role as an effective hydrogen donor. For the SEI experiments, the N2 flow rate was fixed at 10 SCCM. Raising the SEI from 240 to 306 kJ L−1 increased the NH3 yield from 57.6 to 97.2 μmol h−1 (Fig. 3b). This enhancement likely arises from the stronger plasma-induced fragmentation and activation of gaseous reactants and HDPE at higher SEI, leading to higher densities of reactive species and more productive collisions for NH3 formation.19,20 The energy efficiency also showed a modest increase with SEI, suggesting that the additional energy input was still effectively utilized for the target reaction within the investigated range. In contrast, when SEI was varied by changing the gas flow rate under fixed applied input power (Fig. S10), different trends were observed, indicating that the apparent SEI effect is coupled with the experimental parameter used to vary it. In particular, varying the flow rate also changes the gas throughput, the residence time in the discharge zone, and the capture behavior of NH3 in the downstream acid solution. A comparison table has been added to summarize NH3 yield and energy efficiency for representative reports in related fields (Table S2). The table shows that, although plasma routes can achieve relatively high NH3 yields among electrified NH3 synthesis approaches, their energy consumption remains substantially higher than that of several direct electrocatalytic or Li-mediated routes. Therefore, further progress toward industrially relevant plasma NH3 synthesis requires simultaneous improvement in both NH3 production rate and energy efficiency.
As shown in Fig. 3c and d, the stability of the plasma-assisted NH3 synthesis process from N2, H2O and HDPE was assessed over 6 h. HDPE was fully packed into the reactor. The feeding gas consisted of N2 saturated with 2.64 mol% H2O at a flow rate of 10 SCCM, and the input power was 40 W. During the experiments, plasma stability and steady-state operation were assessed by monitoring the temperature of the plasma zone with an infrared thermal camera (TOPDON TC002C), the concentration of gaseous byproducts detected by micro-GC, and the current reading displayed on the plasma generator. Throughout the stability test, NH3 continued to accumulate at a comparable rate over time. Notably, the elevated yields of gaseous products within the first hour suggest more active HDPE decomposition, as carbonaceous gas yields reflect the extent of polymer fragmentation. This is attributed to the direct exposure of fresh HDPE surfaces to reactive plasma species, which promotes rapid chain scission. Subsequently, gradual surface oxidation introduces oxygen-containing functional groups that partially passivate the polymer surface and reduce the accessibility of fresh chains to reactive species. As a result, the yields of NH3 and gaseous byproducts decreased after the first hour and then remained stable over the subsequent five hours. Additionally, gaseous products were generated steadily over the subsequent five hours, predominantly H2, CO, CH4, and C2H6, with production rates of 1020.3, 359.6, 91.3 and 29.7 μmol h−1, respectively.
Analysis of the liquid products retained in the DBD reactor by 1H NMR (Fig. 4a) revealed alkyl chains as the dominant constituents, indicating that these liquids likely originated from chain scission of HDPE. As the reaction time increased from 30 to 60 minutes, both the number and intensity of alkyl chain signals significantly increased. GC-MS analysis was then employed to determine the carbon chain length distribution (Fig. 4b). The results demonstrated a rise in the relative abundance of C4–C8 products with extended reaction time, consistent with progressive fragmentation of longer hydrocarbon chains. In addition, carbon-balance and hydrogen-balance analyses were performed for the 1 h reaction under the full-packing condition (Tables S3 and S4). The carbon balance gave an error of 5.52%, while the hydrogen balance gave an error of 8.18%, indicating reasonably good closure of the main measured products under the present reaction conditions. Moreover, the NH3 yield increased with increasing HDPE mass loss (Fig. S11), suggesting that NH3 formation is associated with HDPE consumption. At the same time, since only a small fraction of the available hydrogen is ultimately incorporated into NH3, HDPE should be regarded as an auxiliary hydrogen donor rather than a highly selective hydrogen source for NH3 formation.
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| Fig. 4 Liquid products from HDPE treated with plasma for 30 and 60 min, characterized by (a) 1H NMR and (b) GC-MS. | ||
An HDPE-derived solid was also analyzed to elucidate the interactions among HDPE, N2, and H2O. SEM imaging revealed the formation of numerous surface defects on HDPE after plasma treatment, indicating that the plasma-induced decomposition was predominantly a surface process rather than bulk degradation (Fig. 5a and b). FTIR analysis was performed to track surface functional group evolution during a 1 h reaction. As shown in Fig. 5c, characteristic peaks corresponding to C–H stretching (3000–2800 cm−1), methylene bending (1462 cm−1), and methylene rocking vibration (720 cm−1) were present throughout the reaction.22,23 A gradual decrease in peak intensities with time indicated C–H and C–C bond cleavage in HDPE.24 A new absorption band at 3440 cm−1, attributable to –OH groups, emerged and intensified over time, suggesting adsorption of O or OH species originating from H2O dissociation. XPS analysis was conducted to further examine surface chemical changes before and after plasma exposure (Fig. 5d and e). The O 1s spectrum of the fresh HDPE indicated the presence of oxygen-containing species (mainly C
O), likely from surface oxidation or oxygen-containing additives. After 60 min of plasma treatment, the relative intensities of C–O (533.2 eV) and C
O (532.3 eV) peaks increased markedly,23 confirming the adsorption of O atoms generated from H2O dissociation. The C 1s spectrum showed a decline in the C–C peak, and the overall C/O ratio decreased from 16.9 to 4.2. These results further indicate that HDPE not only serves as a hydrogen source but also acts as an oxygen scavenger in the discharge environment, thereby promoting H2O dissociation and suppressing the combination of O atoms with N or H atoms, both contributing to enhanced NH3 yield.
Operando optical emission spectroscopy (OES, AvaSpec-ULS4096CL-EVO, AVANTES) was employed to identify active plasma species. As shown in Fig. 5f, the OES spectra of both the empty-tube and HDPE-packed discharges are dominated by the second positive system (SPS) of N2, corresponding to the C3Πu → B3Πg transition, indicating the presence of electronically excited N2 species in the plasma. Compared with the empty-tube case, the HDPE-packed discharge exhibits substantially enhanced emission intensity, suggesting a stronger discharge and higher population of excited species. A distinct CN emission near 387 nm is observed only for the plastic-packed case, indicating the formation of carbon-containing plasma species arising from the interaction between the discharge and HDPE (Fig. S12).25 In addition, Hβ emission is also observed, consistent with the generation of hydrogen-containing reactive species in the plasma.26 Overall, these results confirm that packing HDPE significantly alters the discharge chemistry and promotes the formation of a richer pool of excited nitrogen, hydrogen, and carbon-containing species relevant to NH3 synthesis and concurrent plastic conversion.
Based on the results described above, the reaction mechanism for NH3 synthesis and the formation of other gaseous and liquid byproducts is proposed, as illustrated in Fig. 6. During plasma discharge, high-energy electrons induce the scission of HDPE chains, generating small radicals, primarily H˙ and ˙CH3, as well as liquid alkanes, which can subsequently decompose into smaller radicals. These reactive species can combine with each other to generate gaseous products such as H2, CH4, C2H6, and C2H4. Concurrently, N2 molecules are excited to N2+ electronic states, which can react with H radicals to form NH3. Upon introducing H2O into the reactor, it undergoes electron-impact dissociation, generating additional H radicals as well as O-containing species. There are three main pathways for consuming O species. First, O species can be adsorbed on the HDPE surface, thereby suppressing H/O recombination and significantly increasing the concentration of H radicals in the plasma. Second, part of the O species can react with carbon fragments derived from HDPE, forming CO and CO2. Third, a fraction of the O radicals may also react with N2+ to produce NOx species (absorbed in aqueous solution, generating NO3− and NO2−), although their yield remains limited.
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