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Article

Effect of Temperature and Mineral Matter on the Formation of NOx Precursors during Fast Pyrolysis of 2,5-Diketopiperazine

National Engineering Laboratory for Biomass Power Generation Equipment, North China Electric Power University, Beijing 102206, China
*
Author to whom correspondence should be addressed.
Energies 2018, 11(3), 629; https://doi.org/10.3390/en11030629
Submission received: 11 February 2018 / Revised: 7 March 2018 / Accepted: 8 March 2018 / Published: 12 March 2018

Abstract

:
2,5-diketopiperazine (DKP) was used as a N-containing model compound to investigate the formation pathway of NOx precursors (HCN, NH3, and HNCO) during biomass pyrolysis. The experiment was carried out using a tube furnace coupled with a Fourier Transform Infrared Spectrometer in an argon atmosphere. The results showed that NH3, HCN, and HNCO were the major N-containing species formed during DKP fast pyrolysis. The largest yield was HCN, followed by NH3 and lastly HNCO. When the pyrolysis temperature was increased, the yield of NH3 increased slowly, but the yield of HCN decreased slightly at 800~950 °C and the change accelerate rapidly above 950 °C. Then NH3 became the main product above 1020 °C. The temperature influence was negligible on the selectivity between HCN and NH3 from pyrolysis of DKP. H radicals played an important role in competitive reactions. It was also noted that the presence of Na+, K+, Ca2+, and Mg2+ exhibited a catalytic effect on nitrogen conversion during the DKP fast pyrolysis process. K+ and Na+ were beneficial to the yield of NH3, but not to the yield of HCN. Ca2+ and Mg2+ could promote the formation of HCN, but prevent the formation of NH3.

1. Introduction

The combustion of biomass usually produces harmful nitrogen oxides due to the high nitrogen content of the biomass, which threatens the environment. Therefore, the study of the conversion of fuel nitrogen in the process of biomass combustion utilization has attracted wide public interest [1,2,3,4,5]. Due to the complex composition and diverse form of the molecules containing nitrogen in biomass, it is difficult to confirm migration mechanisms of the fuel nitrogen by direct pyrolysis of the biomass [6]. In an alternative approach, many researchers have used model compounds with defined molecular structures to study the transformation mechanism of fuel nitrogen in biomass [2,3,7,8]. Many amino acids have been selected as model compounds, since protein is one of the major nitrogen-containing materials in biomass, and a large group of organic molecules is formed by amino acid condensation water reaction. Pyrolysis of the protein generates 3-R,6-R′-2,5-Diketopiperazine (DKPs) [9,10,11,12,13] via peptide bond cleavage. Although the primary reaction of amino acid pyrolysis is formation of DKPs, there are also other reaction pathways, including deamination, dehydration, and decarboxylase [14,15,16,17] during pyrolysis. Therefore, the pyrolysis reactions of amino acids may be inconsistent with those of proteins in biomass. Therefore, recently, 2,5-diketopiperazine (DKP), the simplest DKP, has often been used as a model compound for the study of biomass pyrolysis [3,9].
Hansson et al. [9] investigated the gas release from a fast pyrolysis of the DKP in fluidized bed reactor and demonstrated that the primary pyrolysis gases containing nitrogen were HCN, NH3, and HNCO. The yield of HCN was larger than that of NH3, and the yield of HNCO was the least. In our previous work [3], a TG-FTIR test system was used to study slow heating pyrolysis of DKP. Our results showed that although the NH3, HCN and HNCO were the primary nitrogenous gases released during DKP pyrolysis, the yield of NH3 was the largest, followed by those of HCN and HNCO. The distribution of nitrogen-containing gases released from DKP pyrolysis was almost the opposite under the two different experiment conditions. The release of tar was dependent on the particle diameter of DKP and the heating rate of the fuel, which further influenced the distribution of fuel nitrogen in gaseous products [4,18,19,20,21]. In addition, DKP was put into the reactor in different ways in Hansson’s [9] and our experiments [3]. It is difficult to confirm the mechanism of DKP pyrolysis, because temperature field difference in the DKP particles results in pyrolysis products that influence each other. NH3 is the main product of amino acid and DKP pyrolysis [3,9,22,23]. Amino acids mainly generate NH3 by deamination or amine hydrogenation [17,24], but studies on rapid DKP pyrolysis have not provided the generation pathways of NH3 [7,9,25]. In slow pyrolysis, some scholars [3,26] believe that under the catalytic action of char, H radicals react with char nitrogen to generate NH3. However, in rapid pyrolysis, there is little char formation, so it is necessary to study the generation pathways of NH3 in the rapid pyrolysis of DKP.
This study intends to confirm the migration mechanism of the formation of NOx precursors during rapid pyrolysis of DKP. In order to reduce the influence of the DKP particle diameter, a DKP solution spray reactor was used, since the moisture content of biomass is of a higher level [27], and H2O is stable below 2500 K [28]. The distribution of NOx precursors in the product was investigated during rapid pyrolysis of the DKP.
There are some mineral elements in biomass that have certain catalytic effects on the pyrolysis of biomass nitrogen. Reports on the rapid pyrolysis of a mix of DKP and mineral elements have not been found to date. For information about the mechanism of protein pyrolysis, the effects of the presence of K+, Na+, Ca2+, and Mg2+ on the gas-N release of DKP were examined. The results suggested that the temperature influence was negligible, while H radicals might play an important role in the selectivity of HCN and NH3. K+, Na+, Ca2+, and Mg2+ effected the NOx precursors release during DKP pyrolysis.

2. Experimental

2.1. Apparatus

Pyrolysis experiments were carried out using a tube furnace reactor coupled with a Fourier Transform Infrared (FTIR) spectrometer. Figure 1 shows a schematic diagram of the fast pyrolysis system. The reactor was made of a cylindrical quartz tube with an inner diameter of 25 mm and a length of 800 mm. The reactor tube was placed in a vertical tube furnace, the temperature of which was determined by a heating power controller. To ensure that the sample could be sent evenly into the pyrolysis zone, a quartz glass spray nozzle was selected as an entrance of carrier gas and sample solution. The sample solution was sent into the spray nozzle by a piston metering pump, and the solution was sprayed into the reactor under the drive of carrier gas. The experiment was performed in argon, which was used as a carrier gas, as well as the background atmosphere of the pyrolysis. The flow rate of the argon was controlled by the mass flow controller (MFC). Reaction gases were withdrawn from the bottom of the reactor, and then transported into the FTIR system by a heated transfer pipe at 180 °C. A high-performance FTIR (ABB, MB3000) was used for gas analyses. The FTIR spectra were obtained at wavelengths between 450 and 4000 cm−1 and a resolution of 8 cm−1. The FTIR was calibrated before the experiment and simultaneously detects C2H4, CH4, CO, CO2, HCN, HNCO, NH3, NO, NO2, and other gases. A linear relation between a given wave number absorbance (A) and concentration (c) of gas compounds is expected in an ideal case. Gas specific absorptivity (a) is a function of the wavenumber and can be calculated in a standard sample test. The concentration of the test gas is determined according to the Beer–Lambert Law (A = abc) [10,29], where b is the optical path length (cm). The FTIR data are recorded and transformed into the volume concentration of the gas by analyzing the software automatically.

2.2. Materials

DKP (purity > 99%), NaCl, KCl, MgCl2, and CaCl2·2H2O (purity > 98%) were purchased from Alfa Aesar (China) Chemical Co., Ltd. (Shanghai, China). Three groups of DKP solutions were needed in this study. The first was a pure DKP solution at a concentration of 5 mg/L by dissolving DKP in deionized water. The second group included four DKP solutions. In solution A, NaCl content of 4 wt % of DKP was added to the original DKP solutions (5 mg/L). In solution B, solution C, and solution D, KCl, MgCl2, and CaCl2·2H2O were added, respectively, to the original DKP solutions in the same amount as solution A. The last solution contained the four minerals in the original DKP solution (5 mg/L) prepared with element contents of K 3.88 wt %, Na 0.34 wt %, Ca 1.05 wt %, and Mg 0.77 wt %, in accordance with the content of the elements in rice straw in China as a model biomass system [30].

2.3. Pyrolysis Experiments

The carrier gas in the experiment was high-purity argon (>99.999%). The argon flow rate was 1 L/min. The flow rate of the piston metering pump was 1 mL/min. The total concentration of gas-phase nitrogen (Gas-N) is theoretically 196 ppm if DKP is completely converted into NOx. Content of H2O is 12.4% (v/v), which is similar, on an average, to the exhaust gas from a biomass combustion boiler.
Combustion temperature in a biomass boiler is usually no more than 1000 °C. Therefore, the pyrolysis experiments were performed at eight temperatures (700 °C, 750 °C, 800 °C, 850 °C, 900 °C, 950 °C, 1000 °C, and 1050 °C). The tube furnace was heated to the set point. The FTIR was powered on at the gas cell temperature of 250 °C and 980 mbar. Then, the metering pump was turned on to spray the DKP solution into the reactor. The data measured by the FTIR should be held steady for at least last 15 min. The arithmetic mean of the 5 data in stable condition was determined as the final experimental data. All experiments were conducted in two runs, and the error was within 5%.

3. Results and Discussion

3.1. Distribution of Gas-N Products for Fast DKP Pyrolysis under Stable Temperature

The FTIR spectrum of the small molecular gaseous species of DKP pyrolysis is shown in Figure 2. The primary gaseous products, including HCN, NH3, H2O, HNCO, and CO2, are easily identified by their characteristic absorbance: HCN at 714 cm−1; NH3 at 966 cm−1; H2O at 1500~1600 cm−1; HNCO at 2250 cm−1, and CO2 at 2358 cm−1.
The amounts of C2H4, CO and CO2 were nearly equal to each other. The content of H2O was the largest, at approximately 12.4% (v/v). Most of the water was introduced by the sample solution, and only very little was released from pyrolysis. HCN, HNCO, NH3 and NO were the main Gas-N species, which were the focus of this study.
Figure 3 indicates the yield of HCN, HNCO, NH3 and NO at different pyrolysis temperatures. It was found that HCN exhibited the largest yield, at above 110 ppm, as the main nitrogen product in all of the Gas-Ns at 700~900 °C. The yield of HCN increased gradually with the increase of temperature. The output of HCN decreased slowly at 800~950 °C and then declined rapidly when the temperature was greater than 950 °C. The yield of NH3 was relatively less than HCN, and decreased slightly with the increase of temperature 700~800 °C. At 800 °C, the yield of NH3 reached its lowest amount at 47.53 ppm and then began to ascend slowly at 800~950 °C, then suddenly and rapidly rising at 950 °C. The yield of HNCO was relatively small, but HNCO demonstrated a different behavior when the temperature was changed. The yield of HNCO decreased slowly at 700~850 °C and reached a local minimum point of 7.50 ppm at 850 °C. However, it began to rise again to its highest point, 14.79 ppm, at 1000 °C before decreasing again. The Gas-N release of DKP pyrolysis at 700~850 °C in this study was nearly the same as the results reported by Hansson et al. [9]. In their study, the yield of NH3 was always higher than that of HNCO, but less than HNCO below 800 °C. However, the two studies showed different results at 800~1050 °C. In Hansson’s study [9], the yield rose with the increase of the temperature. The change of the HCN yield was slow. The yield of NH3 rose slightly. On the other hand, our results showed that the yield of HCN began to decline slowly at 800 °C. The yield of NH3 began to rise slowly at 800 °C, but the increase suddenly began to speed up at 950 °C. The total yield of nitrogenous compounds in Gas-N was 180~200 ppm at the pyrolysis temperature, which was equal to the nitrogen content of the DKP added into the rector. These results clearly demonstrated the competitive relationship between different reaction paths to NH3 or HCN during the pyrolysis of DKP. No similar phenomena were reported in Hansson [9] or other previous work [17,31]. These results illustrated the accuracy of the experimental method in our study.
The distribution of Gas-N products from the pyrolysis in this study was quite different from our previous study [3] of the pyrolysis of DKP using the TG-FTIR device, as well as from other [3,9,17,31] pyrolysis studies of DKP or Glycine. A summary of previous work is given in Table 1.
DKP is a cyclo dipeptide compound formed by intermolecular dehydration between two glycines, and the main primary product of glycine pyrolysis [14,15,16,17] is DKP. Simmonds et al. [17] rapidly pyrolyzed model compounds of glycine. Although DKP is the primary pyrolysis product of glycine, other products were also formed through intramolecular dehydration, decarboxylation, and deamination reaction, so there were great differences between the yields of gas-N released from DKP pyrolysis in this study and from glycine pyrolysis in Simmonds et al. [17].
Zhou et al. [3] pyrolyzed DKP using a thermogravimetric analyzer (TGA). Because the samples were stacked in a crucible, the internal volatiles of the DKP particles encountered larger resistance during the escape process, and were polymerized into char [32]. The DKP char produced more NH3, so the yield of NH3 was higher than of HCN in the Zhou et al. [3] study.
Ren [31] investigated Gas-N release of glycine pyrolysis. Because the samples were stacked in a ceramic boat heated in the tube furnace, the thermal resistance of the samples was also higher. The experiment was closer to slow pyrolysis and resulted in the formation of more char nitrogen, from which it is easier to generate NH3 [33], as shown in Figure 4.
The low-temperature tar of DKP pyrolysis may affect the Gas-N distribution. If tar cracking occurs quickly, pyrolysis of DKP will produce more HCN, and if the tar was polymerized to produce char, the pyrolysis of DKP transformed mainly to NH3.

3.2. Decomposition Path Analysis of Fast Pyrolysis DKP

Our previous study [3] reported that DKP pyrolysis occurs in two stages. At the first stage, the majority of the DKP molecules are split into small molecules [25], and a small amount of DKP molecules is polymerized to produce char [31], as illustrated in Figure 4. At the second stage, the small molecules generate Gas-N, hydrocarbons, and carbon oxide compounds, as shown in Figure 5.
Figure 5 shows that due to the symmetry of the DKP molecule, the bond breaks from the first and third positions will generate the same product lactone. However, if there are many H radicals around the DKP molecules, DKP will generate 2-Aminoacetaldehyde by the first reaction pathway.
When the DKP was rapidly pyrolyzed in this study, the main reaction pathway to form HCN fragments was the second path in Figure 5, and only a little HCN was produced from the third path in Figure 6. HNCO and CH2 radicals are produced through lactone. The reaction of CH2 radicals and H radicals may form CH4, and the yield of CH4 was about 10~20 ppm in our experiment. This suggested that some DKP had produced HNCO and CH2 via lactone. The main pathway for generating NH3 is the first pathway, but this requires H radicals to break the C-N bonds. Therefore, the yield of NH3 is relatively small at the low-temperature stage because of the lack of H radicals in the reaction.
However, a different behavior was exhibited at the high-temperature stage. H2O molecules might crack on the surface of the quartz reactor, producing a large number of H and OH radicals [34,35]. In the experiment, the yield of HCN began to decrease rapidly at 950 °C, and that of NH3 increased sharply due to the mass production of H radicals by water. The pyrolysis pathway of DKP transfers from the second or third path to the first path in Figure 5.
It has previously been reported [26] that HCN can be combined with H free radicals to produce NH3 at high temperatures with a catalyst of char. However, a DKP solution was used in our experiment, and therefore, the DKPs almost completely transformed into gas without the formation of coke, according to nitrogen balance estimations. Therefore, it was almost impossible for HCN to produce NH3 directly.

3.3. Analysis of the Catalytic Effect of Minerals on Rapid Pyrolysis of DKP

Minerals are important components of biomass [36,37]. Minerals have an important influence on the distribution of nitrogen-containing compounds released from biomass pyrolysis [29,38,39,40,41,42]. Figure 6 shows that mineral matter has a significant effect on the formation of major Gas-N release from fast pyrolysis of DKP.
Figure 6 shows that the total amounts of the three nitrogen-containing gases—HCN, HNCO and NH3—exhibit little change after minerals were added into the DKP solution, which is in agreement with observations in the literature [29]. However, the yields of different gaseous products changed significantly. Magnesium and calcium promoted the formation of HCN and HNCO and inhibited that of NH3 [37].
The elements potassium and sodium promoted the formation of NH3 and inhibited HCN formation. Little effect was found on the formation of HNCO. It was also found that the promotion and inhabitation of Gas-N were significant at the pyrolysis of DKP that was added into the mixture of four minerals. The catalysis of the mixture was closer to the catalysis of the mineral potassium, which was the most mineral according to the proportion of mineral elements in the biomass, in which the proportion of potassium is largest, followed by calcium and sodium. The total amount of mineral elements was increased, and hence the promotion effect was enhanced [29].
Figure 7 shows the yield change of NOx precursors released from fast pyrolysis DKP blended with potassium at different temperatures. Symbols marked K stand for gas from pyrolysis of DKP mixed KCl. After adding KCl to DKP, the yield trend of gas release from fast pyrolysis of DKP did not change. Potassium promotes N-conversion to NH3 and decreases the formation of HCN at the temperature of 800~1000 °C, and catalysis to HCN reaches its maximum value at around of 900 °C.
These observations suggest that Ca2+ and Mg2+ addition enhances HCN formation during pyrolysis of DKP by intermediates Ca(CN)2 and Mg(CN)2, which are stable chemical compounds [43]. Cl- from additions CaCl2 or MgCl2 in this study would promote Ca(CN)2 and Mg(CN)2 transformation into HCN at high temperature [42]. It is likely that HCN is formed through the following reaction:
Ca 2 + +   2   R-C-N 2 R + Ca ( CN ) 2 + 2 H + 2 HCN   +   Ca 2 +
CaCl2 or MgCl2 cannot catalyze HCN to form NH3, as that of CaO or Ca(OH)2 [41,42,44]. It suggests that CaCl2 or MgCl2 are able to enhance DKP pyrolysis reactions via the second and the third pathways in Figure 5.
The effects of the K+ and Na+ on DKP pyrolysis are different from that of Ca2+ and Mg2+. KCN and NaCN are unstable compounds at 800 °C and cannot generate HCN through KCN and NaCN intermediates [45]. However, at a lower temperature such as 700 °C, some of the HCN may be evolved through the intermediates of NaCN and KCN. As can be seen in Figure 7, the yield of HCN formation from DKP mixed K+ exceeded that of HCN formation from DKP without any additives at 700 °C. Na+ or K+ can also promote the decomposition of tar to produce NH3 [40,43]. The NH3 increase resulting from the addition of Na+ or K+ originates mostly tar-N decomposition [45]. DKP is similar to the tar structure, which may be the reason why Na+ and K+ promote NH3 generation.

4. Conclusions

DKPs are ideal model compounds for studying the mechanism of NOx generation in biomass combustion. The main gaseous nitrogen-containing substances released from fast glycine-DKP pyrolysis are HCN, NH3 and HNCO. The yield of HCN is the highest, and that of HNCO is the lowest. The temperature influence is poor on the selectivity between HCN and NH3 produced from pyrolysis of DKP. H radicals might play an important role in promoting DKP to produce 2-Aminoacetaldehyde and further conversion to NH3.
K+, Na+, Ca2+, and Mg2+ play a catalytic role in the transformation of nitrogen from DKP fast pyrolysis. K+ and Na+ promote the formation of NH3, inhibit HCN and had little effect on HNCO. Ca2+ and Mg2+ have a significant effect on the release of HCN and HNCO and have an inhibitory effect on NH3.

Acknowledgments

The project was supported by the National Basic Research Program of China (973 Program, 2015CB251501) and the Fundamental Research Funds for Central Universities (2018ZD08, 2018MS033).

Author Contributions

Jianqiang Zhou and Pan Gao conceived and designed the experiments; Jianqiang Zhou performed the experiments; Jianqiang Zhou and Pan Gao analyzed the data; Changqing Dong contributed reagents, materials, analysis tools; Jianqiang Zhou wrote the paper; Yongping Yang performed manuscript review. All authors have read and approved the content of the manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. The schematic diagram of the fast pyrolysis system.
Figure 1. The schematic diagram of the fast pyrolysis system.
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Figure 2. The FTIR spectra of the evolved gas from pyrolysis of DKP at 700 °C.
Figure 2. The FTIR spectra of the evolved gas from pyrolysis of DKP at 700 °C.
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Figure 3. Effects of pyrolysis temperature on product yields.
Figure 3. Effects of pyrolysis temperature on product yields.
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Figure 4. Dehydration reaction between two DKP molecules.
Figure 4. Dehydration reaction between two DKP molecules.
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Figure 5. The potential pathway for pyrolysis of DKP.
Figure 5. The potential pathway for pyrolysis of DKP.
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Figure 6. Effect of included mineral matter on NOx precursor release from DKP prolysis.
Figure 6. Effect of included mineral matter on NOx precursor release from DKP prolysis.
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Figure 7. Yield of N-containing species from DKP pyrolysis, including KCl.
Figure 7. Yield of N-containing species from DKP pyrolysis, including KCl.
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Table 1. Yields of Gas-N from pyrolysis of the nitrogen-containing model.
Table 1. Yields of Gas-N from pyrolysis of the nitrogen-containing model.
SamplePyrolysis DeviceHeating RateTemperature/°CGas-N/%Reference
HCNNH3HNCO
GlycineQuartz tubeFast80043.746.49.9[31]
GlycineGC-MSFast50041.059.0n.a.[17]
DKPTG-FTIRSlow20~80028.654.317.1[3]
DKPFluidized bedFast80079912[9]
DKPQuartz tubeFast80069.225.15.7This study
n.a.—no anlysis.

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MDPI and ACS Style

Zhou, J.; Gao, P.; Dong, C.; Yang, Y. Effect of Temperature and Mineral Matter on the Formation of NOx Precursors during Fast Pyrolysis of 2,5-Diketopiperazine. Energies 2018, 11, 629. https://doi.org/10.3390/en11030629

AMA Style

Zhou J, Gao P, Dong C, Yang Y. Effect of Temperature and Mineral Matter on the Formation of NOx Precursors during Fast Pyrolysis of 2,5-Diketopiperazine. Energies. 2018; 11(3):629. https://doi.org/10.3390/en11030629

Chicago/Turabian Style

Zhou, Jianqiang, Pan Gao, Changqing Dong, and Yongping Yang. 2018. "Effect of Temperature and Mineral Matter on the Formation of NOx Precursors during Fast Pyrolysis of 2,5-Diketopiperazine" Energies 11, no. 3: 629. https://doi.org/10.3390/en11030629

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