ACS Publications. Most Trusted. Most Cited. Most Read
Ammonia Concentrator for Repeatable Adsorption/Desorption Using Nickel Hexacyanoferrate as Adsorbent and Production of Solid Ammonium Bicarbonate
My Activity

Figure 1Loading Img
  • Open Access
Research Article

Ammonia Concentrator for Repeatable Adsorption/Desorption Using Nickel Hexacyanoferrate as Adsorbent and Production of Solid Ammonium Bicarbonate
Click to copy article linkArticle link copied!

  • Hatsuho Usuda*
    Hatsuho Usuda
    National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
    *Email: [email protected]. Phone: +81-29-861-3650.
  • Tomoji Watanabe
    Tomoji Watanabe
    National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
  • Takamitsu Ishikawa
    Takamitsu Ishikawa
    National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
  • Naoki Nakashima
    Naoki Nakashima
    National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
  • Keiko Noda
    Keiko Noda
    National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
    More by Keiko Noda
  • Akira Takahashi
    Akira Takahashi
    National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
  • Tohru Kawamoto*
    Tohru Kawamoto
    National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
    *Email: [email protected]. Phone: +81-29-861-5141.
  • Kimitaka Minami*
    Kimitaka Minami
    National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
    *Email: [email protected]. Phone: +81-29-861-3108.
Open PDFSupporting Information (1)

ACS Sustainable Chemistry & Engineering

Cite this: ACS Sustainable Chem. Eng. 2024, 12, 6, 2183–2190
Click to copy citationCitation copied!
https://doi.org/10.1021/acssuschemeng.3c05679
Published January 30, 2024

Copyright © 2024 The Authors. Published by American Chemical Society. This publication is licensed under

CC-BY-NC-ND 4.0 .

Abstract

Click to copy section linkSection link copied!

Ammonia serves as both a valuable substance and an environmental pollutant. Its recovery and reuse offer a promising approach to mitigate environmental impacts while reducing costs for treatment, production, and CO2 emissions. In this article, we present a flow system to develop efficient methods for the recovery and reuse of ammonia. In this system, adsorption and desorption were subsequently conducted without relocating the adsorbent column. In the experiment, the adsorbent was composed of nickel hexacyanoferrate (NiHCF) granules, the inlet gas contained approximately 19,000 ppm of NH3 in the air, and the washing liquid for the desorption was NH4HCO3 solution. The outlet NH3 concentration decreased to 3 vol % of the inlet at first and then gradually increased. During desorption, ammonium concentration in the washing liquid increased, and the pH was kept around 8 due to CO2 introduction. After the adsorption and desorption cycles, the washing liquid was cooled to 5 °C, and a NH4HCO3 solid was precipitated. Moreover, NH4HCO3 solid was obtained inasmuch as the adsorbed amount after repeating the adsorption and desorption several times. This study demonstrates the continuous operation of adsorption and desorption cycles and that NiHCF granules can adsorb and desorb NH3 repeatedly.

This publication is licensed under

CC-BY-NC-ND 4.0 .
  • cc licence
  • by licence
  • nc licence
  • nd licence
Copyright © 2024 The Authors. Published by American Chemical Society

Synopsis

Ammonia concentrator enabled repeatable adsorption from the air, desorption into a liquid, and production of solid ammonium bicarbonate.e

Introduction

Click to copy section linkSection link copied!

Nitrogen compounds are crucial substances in industries and agriculture. One of the nitrogen compounds, ammonia (NH3), is generated at an approximate annual production rate of 180 million metric tons. (1) The majority of NH3 is synthesized from atmospheric nitrogen (N2) using the Haber-Bosch process, which results in the emission of approximately 451 million tons of CO2, accounting for approximately 1% of global annual CO2 emissions as of 2010. (2) The produced ammonia serves as a fundamental component in the synthesis of various industrial products and fertilizers, significantly contributing to the augmentation of crop yields. Following the utilization of NH3, however, nitrogen compounds are released into the environment through wastewater, exhaust gases, and in agricultural practices, namely, urine and feces, in diverse forms including NH3, ammonium ions (NH4+), organic nitrogen, nitrate ions (NO3), and NOx, consequently exerting detrimental effects on the environment. (3−6) To mitigate this pollution, denitrification and denitration methods have been created, albeit requiring a certain amount of energy for the conversion of nitrogen compounds back into atmospheric N2. (7,8) In the current artificial nitrogen cycle, substantial energy and a considerable amount of CO2 emissions are required to convert atmospheric nitrogen (N2) into utilizable nitrogen compounds and subsequently revert them through a detoxification process. While the artificial nitrogen cycle has spurred significant advancements in industry and agriculture, its sustainability from a global environmental perspective is questionable.
The development of a sustainable nitrogen cycle is required for significant decreases in energy consumption and CO2 emissions. A key solution toward achieving this sustainability lies in the recovery and reuse of NH3. There are various ways to remove NH3 from waste gas such as water scrubbing, (9) ultraviolet light, (10) catalytic reactions, (11−13) and biofilters, (14−17) but they are not intended for the reuse of NH3. For example, water scrubbing, a commonly employed method for ammonia removal, falls short in terms of selectivity for the efficient reuse of NH3.
Our research group has conducted studies on NH3 recovery and reuse methods using Prussian blue (PB) and Prussian blue analogs (PBAs) as highly selective adsorbents with superior adsorption capacities compared to other ammonia adsorbents. (18−20) PBAs are microporous materials denoted as AyM[M′(CN)6]x (A = Na+, K+, NH4+, etc., M and M′ = Fe, Cu, Co, Ni, Co, etc.) and exhibit characteristic adsorption and desorption characteristics depending on the variations in M, M′, and composition x and y. (21−25) There are two types of adsorption sites in PBAs as shown in Figure 1a. (19) One is the interstitial site, which is a confined space where a positive ion such as potassium and ammonium is preferentially adsorbed, and the other is a vacancy site, which is surrounded by six open metal sites where NH3 and water (H2O) are known to be adsorbed. The use of PBA adsorbents holds promise for NH3 reuse because the adsorbed NH3 can be desorbed through heating or washing with water or specific solutions. (19,25−29) Moreover, the PBA adsorbents have already been applied to discarded ammonia gas and showed a significant decrease in ammonia concentration in the gas. (27,28)

Figure 1

Figure 1. (a) Crystal structure of NiHCF, which has interstitial sites and vacancy sites. (b) Photograph of NiHCF granules.

We attempted washing desorption and subsequent solid recovery for NH3 recovery because ammonium salt offers several advantages as a NH3 species, on the points of energy efficiency and the production of safer products with enhanced portability compared to NH3 gas, liquid NH3, or NH3 solutions. In a previous study, we demonstrated the desorption of adsorbed NH3 on copper hexacyanoferrate (CuHCF), which is a type of PBA, by washing it with a saturated ammonium bicarbonate (NH4HCO3) solution, and the precipitation of NH4HCO3 solid by introducing CO2 gas into the solution. (26) The NH3 desorption characteristics using an NH4HCO3 solution were evaluated for various PBAs, revealing that nickel hexacyanoferrate exhibited a high desorption ratio and structural stability throughout the NH3 adsorption and desorption process. (29) The desorption method utilizing the NH4HCO3 solution has so far been demonstrated only in batch experiments, employing separate equipment for the adsorption and desorption processes. However, the batch operation will not be applicable to the treatment of waste gas that is emitted continuously because it can only treat the gas off-and-on, requiring a lot of labor for its operation. Therefore, it is crucial to develop a system that enables continuous operation for practical applications.
In this study, we perform adsorption and desorption within a continuous flow system, utilizing a gas flow line and a liquid flow line without the need to relocate the adsorbent column. This system will have economic advantages in that it does not require heat for desorption and it does not emit washing liquid as wastewater because the washing liquid can be repeatedly used. In the experiment, the inlet gas contained approximately 19,000 ppmv of NH3 in the air, and the washing liquid for the desorption was NH4HCO3 solution. The NH3 concentration in the inlet gas was determined to be comparable to that in the batch experiment in the previous report, (29) but the applicable concentration will be lowered in a future study. After the adsorption and desorption cycles, the washing liquid was cooled to 5 °C for the precipitation of the NH4HCO3 solid. Nickel hexacyanoferrate (NiHCF) was adopted as an adsorbent because its desorption efficiency and structural stability were proved to be high enough during NH3 adsorption and desorption using NH4HCO3 solution as a washing liquid. (29)

Materials and Methods

Click to copy section linkSection link copied!

Materials

We developed granular NiHCF containing 5 wt % of poly(vinyl alcohol) (PVA) as a binder. NiHCF was synthesized aiming for Ni[Fe(CN)6]0.66 (Figure 1a) where the NH3 desorption occurs in saturated NH4HCO3 solution in the case of NiHCF. (29) The shape of the NiHCF granules was cylindrical with a diameter and length of approximately 5 and 10 mm, respectively (Figure 1b). NH4HCO3 was commercially available from Fujifilm Wako Pure Chemical (Osaka, Japan) and was used without further purification.

Adsorption and Desorption

The experimental setup of NH3 adsorption and desorption is shown in Figure 2. Pressure meters (GC31, NAGANO KEIKI Co., LTD, Tokyo, Japan) and flow meters (FD-XS8, KEYENCE Corp., Osaka, Japan) are denoted as Pn and Fn (n = 1, 2, and 3), respectively. The diaphragm pumps 1 and 2 are FF20KPDC-M, and 3 is NF1.60KTDC. The pumps were commercially available from KNF (Freiburg, Germany). MFC 1, 2, and 3 are mass flow controllers CUBEMFC1005-4S2-50-NH3-CR-003-SWL, CUBEMFC1005-4S2-2L-AIR-003-SWL, and CUBEMFC1005-4S2-50-CO2-003-SWL commercially available from FCON CO., Ltd. (Kochi, Japan). The adsorbent column contained 177 g of NiHCF granules washed with NH4HCO3 solution in advance such that the conditions of NiHCF in the first cycle are similar to those of the second and third cycles.

Figure 2

Figure 2. Experimental setup of the NH3 adsorption and desorption. MFC stands for the mass flow controller. The adsorption and desorption lines are shown as red solid lines with closed arrows, and blue thin lines with open arrows, respectively. The thicker lines and the thinner lines represent gas and liquid lines, respectively. Pn and Fn represent the pressure and flow meter, respectively.

During adsorption, the flow rates of dry air and NH3 were 1970 and 40 mL/min, respectively. Therefore, the NH3 concentration of inlet gas was approximately 19,000 ppmv. H2O concentration was calculated as 31,000 ppmv from vapor pressure and the gas flow rates. NH3, CO2, and H2O concentrations in the outlet gas were measured using Fourier transform infrared red spectroscopy (FTIR) with an OMEGA5 commercially available from Bruker (MA, USA). Its detection limits for NH3, CO2, and H2O were 0.4, 2, and 300 ppmv, respectively. The adsorption was continued until the outlet NH3 concentration reached 95 vol % of the inlet NH3 concentration to obtain breakthrough curves for adsorption behavior; then, the experiment moved to the desorption step.
In the desorption experiment, 700 mL of NH4HCO3 solution was used as the washing liquid, whose initial NH4HCO3 concentration was 1.6 mol/L, which is the saturated concentration at 5 °C. The washing liquid was stored in an NH4HCO3 solution tank and sent to the adsorbent container by pump 1 at flow rates of 25–40 mL/min to wash the NiHCF granules after adsorption. Pump 2 downstream of the adsorbent sends the washing liquid back to the NH4HCO3 solution tank at the same rate as pump 1. A part of the washing liquid was sent into the CO2 tank from the NH4HCO3 solution tank by pump 3 at a flow rate of 120 mL/min in the CO2 tank to make contact with the CO2 gas. The stop valves 1 and 2 were closed to prevent leaks of gases evaporated from the adsorbent and washing liquid during desorption. The stop valve 3 was basically closed throughout the experiment but opened once every 60 min during desorption to collect 1 mL of washing liquid. The collected washing liquid was subjected to pH and K+ concentration measurements using a compact pH meter LAQUAtwin and a compact K+ meter LAQUAtwin (HORIBA, Ltd., Kyoto, Japan), respectively; subsequently, the liquid was diluted twice with a 50 g/L boric solution to prevent NH3 evaporation. The liquid was further diluted 10,000 times with water and filtered using a PTFE membrane filter with a pore size of 0.45 μm (Omnpore, Metrohm) for measurements using ion chromatography (IC), ECO IC (Metrohm AG, Herisau, Switzerland). In the IC, ammonia nitrogen concentration in the samples was measured as ammonium ion because the eluent was 1.7 mmol/L nitric acid/0.7 mmol/L dipicolinic acid and its pH was low, which changes an ammonia molecule to an ammonium ion in solution.
The adsorption and desorption cycle was repeated three times without exchanging the NiHCF granules and washing liquid. After three cycles of adsorption and desorption, the washing liquid was kept at 5 °C to yield precipitate. For the analysis of nickel elution into the washing liquid from the adsorbent granules, an aliquot of the washing liquid was diluted 500 times with 2 wt % nitric acid and filtered using a PTFE membrane filter with a pore size of 0.45 μm. The nickel concentration was measured by using a microwave plasma atomic emission spectrometer (MP-AES, Agilent 4100; Agilent Technologies Japan Ltd.).
The amounts of NH3 species in the NiHCF granules before and after the three cycles of adsorption and desorption were evaluated by washing the granules four times with 0.2 mol/L NaHSO4 solution at a liquid/solid ratio >60 and shaken at 600 rpm for more than 24 h. The granules and solution were then separated through centrifugation at 3000 rpm for 10 min using a 5702 centrifuge 5702 (Eppendorf Co.). The ammonium nitrogen concentration in the supernatant was measured after the filtration using a PTFE membrane filter with a pore size of 0.45 μm and the NH3 species that remained in the NiHCF granules were calculated.

Characterization

To obtain the NH3 adsorption capacity for NiHCF powder in pure NH3, the measurement of the NH3 adsorption isotherm was conducted as follows. First, the hydration water in the NiHCF sample in a sample tube was removed by heat treatment at 150 °C at 10 Pa for 24 h using a pretreatment apparatus (BELPREP VAC MicrotracBEL Inc.). Subsequently, the sample tubes were purged with N2 gas. NH3 isotherms for the NiHCF samples were obtained using a gas-adsorption system (BELSORP-max, MicrotracBEL Inc.) at 25 °C. The criterion of equilibrium in this measurement was a pressure change below 0.3% in 10 min.

Results and Discussion

Click to copy section linkSection link copied!

Adsorbent Information

The crystal structure of synthesized NiHCF (Figure S2a) agreed with the reported NiHCF structures. (30,31) The composition of nickel, hexacyanoferrate, and potassium in the NiHCF granules was Ni:Fe:K = 1:0.69:0.1 (Table S1). The smaller Fe proportion compared to Ni suggests that a [Fe(CN)6]3– vacancy existed. The NH3 isotherm of the NiHCF powder is shown in Figure 3. The adsorbed NH3 amount exceeded 8 mmol/g at the NH3 pressure corresponding to the NH3 partial pressure in the inlet gas in the flow experiment. The NiHCF granules were washed with NH4HCO3 solution, and their XRD profile (Figure S1a), FTIR spectra (Figure S1b), and composition were analyzed. The XRD and FTIR results were comparable with those after NH3 desorption with NH4HCO3 solution. (29) The composition became Ni:Fe:K = 1:0.75:0.0 (Table S1) suggesting that K in NiHCF exchanged with the ammonium ions in the NH4HCO3 solution.

Figure 3

Figure 3. NH3 adsorption isotherms of NiHCF powder at 25 °C. The blue broken line indicates the partial pressure of NH3 in the inlet gas.

Adsorption and Desorption Experiments

The results of the adsorption experiments are plotted in Figure 4a as the NH3 concentrations of the inlet and outlet gas. The inlet NH3 concentration was maintained at approximately 19,000 ppmv throughout the adsorption experiment. The outlet NH3 concentration in the first cycle was at first 490 ppmv meaning that 97 vol % of NH3 was trapped in the adsorbent, and gradually increased, drawing a breakthrough curve until 14.6 h where the outlet NH3 concentration reached more than 95 vol % of inlet NH3 concentration and the experiment moved to a desorption step.

Figure 4

Figure 4. Results of NH3 adsorption and desorption. (a) NH3 concentration of the gas flow getting in/out of the NiHCF adsorbent in the three cycles of adsorption, which have a desorption step after the adsorption. (b) Ammonium nitrogen concentration (blue square) and pH (orange cross) in the washing liquid during desorption.

Discontinuous falls in the breakthrough curve were observed at total flowing gas times of 3.5 and 7.6 h in the first cycle when the experiment was temporarily stopped for more than 12 h because the experiments were conducted only during the day. The falls are considered to be caused by diffusion of NH3 in the granules, resulting in a decrease in the NH3 density around the surface of the NiHCF granules and adsorbed more NH3 when the experiment was repeated than before the experiment was temporarily stopped. The same trends were observed for the second and third cycles.
The outlet NH3 concentrations in the first and second adsorption were approximately 19,000 ppmv right before desorption, and they decreased to 3000 and 4600 ppmv after desorption, respectively, indicating that a part of the trapped NH3 was successfully desorbed into the washing liquid. The initial outlet NH3 concentration in each cycle increased as the cycle increased. The amount of the total trapped NH3 during adsorption was 1420 mmol (1st cycle: 620 mmol, second cycle: 390 mmol, third cycle: 300 mmol), which were calculated from the summation of the gap between the NH3 amounts in the inlet and outlet gases (SI).
CO2 concentrations in the outlet gas were 38,000, 79,000, and 110,000 ppmv at the beginning of each of the first, second, and third adsorption terms, respectively, and immediately decreased to a few thousand ppmv (Figure S3). The amounts of emitted CO2 were 70, 160, and 190 mmol in the first, second, and third adsorption terms, respectively, and the total amount was 420 mmol. The high CO2 concentrations at the beginning are considered to be caused by CO2 evaporated from the washing liquid and stored in the dead volume of the equipment. Another possible CO2 source is the washing liquid on the granule surface, whose amount was too little to afford all of the CO2 emission in the outlet gas. The CO2 evaporation will be reduced by designing the system with little dead volume or improving the CO2-introducing method.
The crystal structure and chemical conditions of the NiHCF granules did not significantly change during the adsorption and desorption experiment (Figure S1). This result is consistent with that of a previous study. (29) The structural stability of NiHCF shows durability in practical use. Moreover, there was no significant difference observed among the granules on the upstream, midstream, and downstream sides in the adsorbent column, which indicates that the gas flowed through the entire column. The composition of nickel and iron became Ni:Fe = 1:0.79 (Table S1). The relative decrease of Ni against Fe is considered to be caused by elution into the washing liquid because Ni was detected at 3000 ppm in the washing liquid, whereas Fe was not.
The desorption results are exhibited in Figure 4b as plots of the ammonium nitrogen concentration and pH in the washing liquid. The initial ammonium nitrogen concentration was 1.6 mol/L, which is approximately the saturated concentration of NH4HCO3 at 5 °C. The final concentration of the first, second, and third cycles were 2.0, 2.5, and 2.7 mol/L, respectively. The increase in the ammonium nitrogen concentration at each cycle indicates that the adsorbed NH3 in the NiHCF granules was successfully desorbed into the washing liquid. In the first cycle, the washing liquid flow was temporarily stopped at the total washing time of 3.5 h, but the ammonium nitrogen concentration was kept constant until the next start. The unchanging concentration shows that the NH3 species did not rapidly escape from the washing liquid. The total amount of NH3 desorbed from the NiHCF granules was 680 mmol (1st cycle: 280 mmol, second cycle: 270 mmol, and third cycle: 130 mmol), indicating that the desorption amount was lower than half of the adsorption amount. The remaining NH3 species in the NiHCF granules was 6.0 mmol/g-adsorbent after the third desorption according to the results of desorption using acid for the NiHCF granules.
The pH increased to 8.1 when desorption started and gradually decreased to 7.9, as shown in Figure 4b. This trend is considered a result of the balance between the CO2 dissolution rate and the NH3 desorption rate. At first, NH3 dissolved in the washing liquid more than CO2 resulting in an increase in the pH; subsequently, as CO2 dissolved, the pH became lower. In this pH region, more than 90% of the NH3 species exist as NH4+ ions, and more than 90% of the CO2 species exist as bicarbonate ions (HCO3) according to the calculation using the dissociation constants of NH3 (pKa = 0.21 (32)), H2CO3 (pKa = 6.35), and HCO3 (pKa = 10.33). (33)
The molar ratio of NH3 and CO2 was calculated from equilibrium constants and pH. Before desorption, the ratio was NH3:CO2 = 16:17; then, it became NH3:CO2 = 27:26 at the end of the third cycle. The NH4 concentration increased through desorption but the change in the molar ratio of NH3 and CO2 was small since CO2 was introduced into the washing liquid simultaneously.
The nickel concentration in the washing liquid was 3200 ppm at the end of cycle 3, which means that 4.8 mol % of nickel was eluted from NiHCF granules into the washing liquid. However, the ammonia concentrator presented in this study does not emit wastewater, and the elution is considered to stop at the equilibrium. Therefore, the elution will not significantly affect the cycle durability of the NiHCF granules.

Precipitation

Precipitation was observed in the washing liquid-cooled to 5 °C after three cycles of the NH3 adsorption and desorption experiment. After washing with ethanol, the color derived from the nickel ions became invisible in the precipitate, as shown in Figure 5a.

Figure 5

Figure 5. (a) Washed precipitate obtained after desorption. (b) FTIR spectra of the obtained precipitate and commercial NH4HCO3.

The FTIR spectra of the obtained precipitate and commercial NH4HCO3 are exhibited in Figure 5b. Both spectra showed comparable features, indicating that the precipitate was NH4HCO3. Possible ammonium salts are ammonium bicarbonate, ammonium carbamate, and ammonium carbonate. The FTIR spectra of the precipitation were comparable to a reported one of ammonium bicarbonate and different from a reported one of ammonium carbamate and ammonium carbonate. (34) The amount of precipitated NH4HCO3 was 300 mmol, which is 36% of the expected amount calculated from the IC result in the saturated concentration at 5 °C. One of water-based adsorption, coupling thermal stripping, and acid absorption can also be a technique to obtain solid ammonium salt as ammonium sulfate. (35) However, it will require five times more energy compared to the cooling precipitation. The alkali-halide salt adsorption is not applicable to real discarded gas that contains water vapor since the alkali-halide salts are usually deliquescent.

Material Balance

The NH3 species in NiHCF granules was 1.9 mmol/g-granule before the first adsorption and most of them are considered to be NH4+ according to the FTIR result in Figure S1b denoted as “washed with NH4HCO3 solution”. This result suggests that NH4+ did not desorb into the NH4HCO3 solution. The NiHCF granules in the column were 177 g, which should have 340 mmol of NH3 species before adsorption. In total, in the first set of the adsorption and desorption experiment, 4050 mmol of NH3 entered into the adsorbent column, and 1310 mmol was trapped in the column; 680 mmol was then desorbed in the washing liquid. The desorbed amount was less than the trapped amount, and the remaining 630 mmol of NH3 species were supposed to be NH4+ mainly (Figure S1b). This tendency agrees well with our previous results. (29) Considering the material balance and the amount of NH3 species in the granules before the first adsorption, 970 (340 + 1310 – 680) mmol of NH3 species should remain in the NiHCF granules. Particularly, the NH3 species in the granules was demonstrated as 1000 mmol, which is comparable to the value calculated from the adsorbed and desorbed amounts. After adsorption in cycle 3, the NH3 species in the adsorbent was calculated as 1130 (1000 + 130) mmol since the desorption amount was 130 mmol. This means that the adsorbed amount per NiHCF granule weight after adsorption in cycle 3 was 6.4 (1130/177) mmol/g-granule, which is 78% of the adsorbed amount in 19,000 ppmv of NH3 gas according to the isotherm in Figure 3. Possible reasons for the gap between the adsorbed amounts in the column experiment and isotherm are as follows: the NH3 has not diffused into the center of the granules yet; the adsorption capacity per weight was decreased owing to the PVA contained in the granules at approximately 5 wt % of their weight.
The bars in Figure 6 show the adsorbed and desorbed amount in the first set (Figure 4) and the second set where the second set of 3 cycles of the adsorption and desorption experiment was conducted in the same protocol as the first set after changing the washing liquid to a new one. Both the adsorption and desorption amounts in the first set decreased as the cycle number increased, suggesting that the adsorption and desorption were hindered as the NH4+ concentration increased in the washing liquid. It was also because the system was turned to desorption from adsorption before the adsorption amount reached saturation. The decrease in the adsorption amount does not mean a lack of sustainability. The adsorption amount should be the same as the desorption amount if all of the NH3 can be desorbed. However, the results indicate that there are two kinds of adsorption sites; one can easily release NH3, and the other cannot as reported in previous research. Moreover, the desorption efficiency was different depending on the NH4+ concentration in the washing liquid. In the first set, the adsorbed NH3 amount in cycle 2 was more than the desorbed amount in cycle 1, indicating that the adsorption capacity was more than the amount adsorbed in cycle 1, and the same trend was observed in cycles 2 and 3 of the first set. The gap between the adsorbed and desorbed amount in Figure 6 was 340, 127, and 164 mmol in cycles 1, 2, and 3, respectively, of the first set. In the second set, the adsorbed amount decreased while the desorbed amount was constant, and finally, in cycle 3, the adsorbed and desorbed NH3 amounts became comparable demonstrating a possibility of NH3 desorption as much as adsorption.

Figure 6

Figure 6. Adsorbed and desorbed NH3 amounts in each cycle. Red bars: adsorbed amount of NH3. blue bars: desorbed amount of NH3. The 2nd set of 3 cycles of the adsorption and desorption experiment was conducted in the same way as the 1st set (Figure 4) after changing the washing liquid used in the 1st set to a new one. The right axis exhibits the NH3 amount normalized by the adsorbent weight. The broken and dotted lines are the adsorbed and desorbed amounts in the reported batch experiment in the case of NiHCF, respectively. (29)

Comparisons with the batch experiment for NiHCF (29) are shown in Figure 6. The adsorption amount was less than that in the batch experiment, as shown in Figure 6. This is because adsorption had not reached saturation when the experiment turned to desorption on the contrary to the batch experiment.
The material balance of the NH3 species in cycle 3 of the second set is shown in Figure 7 to discuss the possibility of constant adsorption and desorption. NH3 was provided to the adsorbent column at 1150 and 920 mmol was not trapped by the NiHCF granules, showing that 230 mmol was once trapped, and the same amount was desorbed into the washing liquid. Afterward, the same amount of NH3 in the washing liquid became solid NH4HCO3. This material balance suggests that after several sets of adsorption, desorption, and precipitation processes, the same amount of NH4HCO3 could be recovered as that of trapped NH3 in the adsorbent. A certain amount of NH3 was lost as outlet gas because adsorption was continued until NH3 concentration in the outlet gas became 95 vol % of that in the inlet gas in this experiment to obtain breakthrough curves. In an application, the double or triple tower system will be adopted, and an adsorbent column can be switched from adsorption to desorption when the NH3 concentration in outlet gas reaches 0.1 vol % or less. This greatly reduces the loss of NH3. The loss also occurs in a batch experiment due to the large dead volume. (26) The loss due to the dead volume will decrease as the size scale of the system becomes larger. However, there is a thermodynamic limit of NH3 loss the dead volume among the NiHCF granules in a column will not be zero even if the size scale of the NH3 concentrator becomes larger. The gas phase in the adsorbent column was 26 vol % which was calculated from the bulk density of NiHCF granules and the density of NiHCF itself. The thermodynamic limit of NH3 loss was less than 0.01 mol % of NH3 trapped in the column when being calculated from the equilibrium of NH3 concentration in the gas phase and the adsorbed NH3 in NiHCF granules.

Figure 7

Figure 7. Material balance of NH3 species during the process of adsorption, desorption, and precipitation in cycle 3 of the 2nd set. The units of the numbers is mmol.

Conclusions

Click to copy section linkSection link copied!

Significant sequential adsorption and desorption of NH3 were proved to be possible using NiHCF granules as an adsorbent and NH4HCO3 solution as the washing liquid. This method enabled a continuous operation of adsorption and desorption compared to a batch process, which requires different sets of equipment for adsorption and desorption. Successful implementation of NH3 adsorption and desorption within this system would demonstrate the feasibility of a two- or multitower-type operation.
The system presented in this study is very economic at the points of no heat desorption and no wastewater. The verification test of this ammonia concentrator will be conducted, and a more detailed economic analysis will be done in the near future.

Supporting Information

Click to copy section linkSection link copied!

The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acssuschemeng.3c05679.

  • Experimental setup of NH3 adsorption and desorption; additional results of characterization of the NiHCF adsorbent; and CO2 concentration in the outlet gas during adsorption (PDF)

Terms & Conditions

Most electronic Supporting Information files are available without a subscription to ACS Web Editions. Such files may be downloaded by article for research use (if there is a public use license linked to the relevant article, that license may permit other uses). Permission may be obtained from ACS for other uses through requests via the RightsLink permission system: http://pubs.acs.org/page/copyright/permissions.html.

Author Information

Click to copy section linkSection link copied!

  • Corresponding Authors
  • Authors
    • Tomoji Watanabe - National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
    • Takamitsu Ishikawa - National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
    • Naoki Nakashima - National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
    • Keiko Noda - National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, Japan
    • Akira Takahashi - National Institute of Advanced Industrial Science and Technology (AIST), Nanomaterials Research Institute, 1-1-1 Higashi, Tsukuba 305-8565, JapanOrcidhttps://orcid.org/0000-0002-8375-7177
  • Author Contributions

    The manuscript was written through contributions of all authors. All authors have given approval to the final version of the manuscript.

  • Funding

    This research was funded by the New Energy and Industrial Technology Development Organization (NEDO; grant number JPNP18016).

  • Notes
    The authors declare no competing financial interest.

Abbreviations

Click to copy section linkSection link copied!

PB

prussian blue

PBA

prussian blue analogs

CuHCF

copper hexacyanoferrate

NiHCF

nickel hexacyanoferrate

PVA

poly(vinyl alcohol)

MFC

mass flow controller

References

Click to copy section linkSection link copied!

This article references 35 other publications.

  1. 1
    U.S. Geological Survey. Nitrogen (Fixed)─Ammonia Miner. Commod. Summ. 2022.
  2. 2
    Boerner, L. K. Industrial Ammonia Production Emits More CO2 than Any Other Chemical-Making Reaction. Chemists Want to Change That Chem. Eng. News 2019, 97(24), https://cen.acs.org/environment/green-chemistry/Industrial-ammonia-production-emits-CO2/97/i24
  3. 3
    Krupa, S. Effects of Atmospheric Ammonia (NH3) on Terrestrial Vegetation: A Review. Environ. Pollut. 2003, 124 (2), 179221,  DOI: 10.1016/S0269-7491(02)00434-7
  4. 4
    Pitcairn, C. E. R.; Leith, I. D.; Sheppard, L. J.; Sutton, M. A.; Fowler, D.; Munro, R. C.; Tang, S.; Wilson, D. The Relationship between Nitrogen Deposition, Species Composition and Foliar Nitrogen Concentrations in Woodland Flora in the Vicinity of Livestock Farms. Environ. Pollut. 1998, 102 (1), 4148,  DOI: 10.1016/S0269-7491(98)80013-4
  5. 5
    Sheppard, L. J.; Leith, I. D.; Crossley, A.; Van Dijk, N.; Fowler, D.; Sutton, M. A.; Woods, C. Stress Responses of Calluna Vulgaris to Reduced and Oxidised N Applied under “Real World Conditions.. Environ. Pollut. 2008, 154 (3), 404413,  DOI: 10.1016/j.envpol.2007.10.040
  6. 6
    van den Berg, L. J. L.; Peters, C. J. H.; Ashmore, M. R.; Roelofs, J. G. M. Reduced Nitrogen Has a Greater Effect than Oxidised Nitrogen on Dry Heathland Vegetation. Environ. Pollut. 2008, 154 (3), 359369,  DOI: 10.1016/j.envpol.2007.11.027
  7. 7
    Nutrient Reduction Technology Cost Estimations for Point Sources in the Chesapeake Bay Watershed Prepared by The Nutrient Reduction Technology Cost Task Force A Stakeholder Group of the Chesapeake Bay Program November 2002 , 2002. https://www.chesapeakebay.net/content/publications/cbp_13140.pdf.
  8. 8
    Mladenović, M.; Paprika, M.; Marinković, A. Denitrification Techniques for Biomass Combustion. Renew. Sustain. Energy Rev. 2018, 82, 33503364,  DOI: 10.1016/j.rser.2017.10.054
  9. 9
    Melse, R. W.; Ogink, N. W. M. Air Scrubbing Techniques for Ammonia and Odor Reduction at Livestock Operations: Review of on-Farm Research in the Netherlands. Trans. Am. Soc. Agric. Eng. 2005, 48 (6), 23032313,  DOI: 10.13031/2013.20094
  10. 10
    Maurer, D. L.; Koziel, J. A. On-Farm Pilot-Scale Testing of Black Ultraviolet Light and Photocatalytic Coating for Mitigation of Odor, Odorous VOCs, and Greenhouse Gases. Chemosphere 2019, 221, 778784,  DOI: 10.1016/j.chemosphere.2019.01.086
  11. 11
    Li, G.; Kanezashi, M.; Yoshioka, T.; Tsuru, T. Ammonia Decomposition in Catalytic Membrane Reactors: Simulation and Experimental Studies. AIChE J. 2013, 59 (1), 168179,  DOI: 10.1002/aic.13794
  12. 12
    Lamb, K. E.; Dolan, M. D.; Kennedy, D. F. Ammonia for Hydrogen Storage; A Review of Catalytic Ammonia Decomposition and Hydrogen Separation and Purification. Int. J. Hydrogen Energy 2019, 44 (7), 35803593,  DOI: 10.1016/j.ijhydene.2018.12.024
  13. 13
    Yin, S. F.; Xu, B. Q.; Zhou, X. P.; Au, C. T. A Mini-Review on Ammonia Decomposition Catalysts for on-Site Generation of Hydrogen for Fuel Cell Applications. Appl. Catal. A Gen. 2004, 277 (1–2), 19,  DOI: 10.1016/j.apcata.2004.09.020
  14. 14
    Bist, R. B.; Subedi, S.; Chai, L.; Yang, X. Ammonia Emissions, Impacts, and Mitigation Strategies for Poultry Production: A Critical Review. J. Environ. Manage. 2023, 328, 116919  DOI: 10.1016/j.jenvman.2022.116919
  15. 15
    Chen, L.; Hoff, S. J.; Koziel, J. A.; Cai, L.; Zelle, B.; Sun, G. Performance Evaluation of a Wood-Chip Based Biofilter Using Solid-Phase Microextraction and Gas Chromatography-Mass Spectroscopy-Olfactometry. Bioresour. Technol. 2008, 99 (16), 77677780,  DOI: 10.1016/j.biortech.2008.01.085
  16. 16
    Chen, L.; Hoff, S.; Cai, L.; Koziel, J.; Zelle, B. Evaluation of Wood Chip-Based Biofilters to Reduce Odor, Hydrogen Sulfide, and Ammonia from Swine Barn Ventilation Air. J. Air Waste Manag. Assoc. 2009, 59 (5), 520530,  DOI: 10.3155/1047-3289.59.5.520
  17. 17
    Peng, F.; Gao, Y.; Zhu, X.; Pang, Q.; Wang, L.; Xu, W.; Yu, J.; Gao, P.; Huang, J.; Cui, Y. Removal of High-Strength Ammonia Nitrogen in Biofilters: Nitrifying Bacterial Community Compositions and Their Effects on Nitrogen Transformation. Water 2020, 12 (3), 712,  DOI: 10.3390/w12030712
  18. 18
    Rieth, A. J.; Dincă, M. Controlled Gas Uptake in Metal–Organic Frameworks with Record Ammonia Sorption. J. Am. Chem. Soc. 2018, 140 (9), 34613466,  DOI: 10.1021/jacs.8b00313
  19. 19
    Takahashi, A.; Tanaka, H.; Parajuli, D.; Nakamura, T.; Minami, K.; Sugiyama, Y.; Hakuta, Y.; Ohkoshi, S.; Kawamoto, T. Historical Pigment Exhibiting Ammonia Gas Capture beyond Standard Adsorbents with Adsorption Sites of Two Kinds. J. Am. Chem. Soc. 2016, 138 (20), 63766379,  DOI: 10.1021/jacs.6b02721
  20. 20
    Van Humbeck, J. F.; McDonald, T. M.; Jing, X.; Wiers, B. M.; Zhu, G.; Long, J. R. Ammonia Capture in Porous Organic Polymers Densely Functionalized with Bro̷nsted Acid Groups. J. Am. Chem. Soc. 2014, 136 (6), 24322440,  DOI: 10.1021/ja4105478
  21. 21
    Welsh, F. S. Particle Characteristics of Prussian Blue in an Historical Oil Paint. J. Am. Inst. Conserv. 1988, 27 (2), 5563,  DOI: 10.1179/019713688806046292
  22. 22
    Loos-Neskovic, C.; Dierkes, M. H. H.; Jackwerth, E.; Fedoroff, M.; Garnier, E. Fixation of Palladium on Insoluble Simple or Complex Cyano Compounds. Hydrometallurgy 1993, 32 (3), 345363,  DOI: 10.1016/0304-386X(93)90046-G
  23. 23
    Manakasettharn, S.; Takahashi, A.; Kawamoto, T.; Noda, K.; Sugiyama, Y.; Nakamura, T. Differences in NH3 Gas Adsorption Behaviors of Metal-Hexacyanoferrate Nanoparticles (M [FeII(CN)6] ·zH2O: M = In3+, Fe3+, and Mn2+). J. Solid State Chem. 2019, 270, 112117,  DOI: 10.1016/j.jssc.2018.10.026
  24. 24
    Parajuli, D.; Kitajima, A.; Takahashi, A.; Tanaka, H.; Ogawa, H.; Hakuta, Y.; Yoshino, K.; Funahashi, T.; Yamaguchi, M.; Osada, M.; Kawamoto, T. Application of Prussian Blue Nanoparticles for the Radioactive Cs Decontamination in Fukushima Region. J. Environ. Radioact. 2016, 151, 233237,  DOI: 10.1016/j.jenvrad.2015.10.014
  25. 25
    Takahashi, A.; Minami, K.; Noda, K.; Sakurai, K.; Kawamoto, T. Trace Ammonia Removal from Air by Selective Adsorbents Reusable with Water. ACS Appl. Mater. Interfaces 2020, 12 (13), 1511515119,  DOI: 10.1021/acsami.9b22384
  26. 26
    Usuda, H.; Sakurai, K.; Takahashi, A.; Kawamoto, T.; Minami, K. Ammonium Salt Production in NH3-CO2-H2O System Using a Highly Selective Adsorbent, Copper Hexacyanoferrate. Environ. Pollut. 2021, 288 (June), 117763  DOI: 10.1016/j.envpol.2021.117763
  27. 27
    Takahashi, A.; Minami, K.; Noda, K.; Sakurai, K.; Kawamoto, T. Harvesting a Solid Fertilizer Directly from Fetid Air. ACS Sustainable Chem. Eng. 2021, 9 (50), 1686516869,  DOI: 10.1021/acssuschemeng.1c06161
  28. 28
    Minami, K.; Takahashi, A.; Sakurai, K.; Mikasa, H.; Takasaki, M.; Doshu, N.; Aoyama, K.; Nakamura, T.; Iwai, R.; Kawamoto, T. Apparatus for Ammonia Removal in Livestock Farms Based on Copper Hexacyanoferrate Granules. Biosyst. Eng. 2022, 216, 98107,  DOI: 10.1016/j.biosystemseng.2022.02.002
  29. 29
    Usuda, H.; Mishima, Y.; Kawamoto, T.; Minami, K. Desorption of Ammonia Adsorbed on Prussian Blue Analogs by Washing with Saturated Ammonium Hydrogen Carbonate Solution. Mol. 2022, 27 (24), 8840,  DOI: 10.3390/molecules27248840
  30. 30
    Wessells, C. D.; Peddada, S. V.; Huggins, R. A.; Cui, Y. Nickel Hexacyanoferrate Nanoparticle Electrodes For Aqueous Sodium and Potassium Ion Batteries. Nano Lett. 2011, 11 (12), 54215425,  DOI: 10.1021/nl203193q
  31. 31
    Shrivastava, A.; Liu, S.; Smith, K. C. Linking Capacity Loss and Retention of Nickel Hexacyanoferrate to a Two-Site Intercalation Mechanism for Aqueous Mg 2+ and Ca 2+ Ions †. Phys. Chem. Chem. Phys. 2019, 21, 2017720188,  DOI: 10.1039/C9CP04115J
  32. 32
    Hall, H. K. Correlation of the Base Strengths of Amines. J. Am. Chem. Soc. 1957, 79 (20), 54415444,  DOI: 10.1021/ja01577a030
  33. 33
    National Astronomical Observatory of Japan. Handbook of Scientific Tables; Maruzen Publishing Co., Ltd., 2012.
  34. 34
    Khanna, R. K.; Moore, M. H. Carbamic Acid: Molecular Structure and IR Spectra. Spectrochim. Acta A Mol. Biomol. Spectrosc. 1999, 55 (5), 961967,  DOI: 10.1016/S1386-1425(98)00228-5
  35. 35
    Tao, W.; Ukwuani, A. T. Coupling Thermal Stripping and Acid Absorption for Ammonia Recovery from Dairy Manure: Ammonia Volatilization Kinetics and Effects of Temperature, PH and Dissolved Solids Content. Chem. Eng. J. 2015, 280, 188196,  DOI: 10.1016/j.cej.2015.05.119

Cited By

Click to copy section linkSection link copied!

This article is cited by 1 publications.

  1. Hanna Fałtynowicz, Jan Kaczmarczyk, Rafał Łużny, Karolina Jaroszewska, Katarzyna Pstrowska, Sylwia Hull, Marek Kułażyński, Karol Postawa. Activated Carbons for Removing Ammonia from Piggery Vent Air: A Promising Tool for Mitigating the Environmental Impact of Large-Scale Pig Breeding. Sustainability 2024, 16 (14) , 6122. https://doi.org/10.3390/su16146122

ACS Sustainable Chemistry & Engineering

Cite this: ACS Sustainable Chem. Eng. 2024, 12, 6, 2183–2190
Click to copy citationCitation copied!
https://doi.org/10.1021/acssuschemeng.3c05679
Published January 30, 2024

Copyright © 2024 The Authors. Published by American Chemical Society. This publication is licensed under

CC-BY-NC-ND 4.0 .

Article Views

1241

Altmetric

-

Citations

Learn about these metrics

Article Views are the COUNTER-compliant sum of full text article downloads since November 2008 (both PDF and HTML) across all institutions and individuals. These metrics are regularly updated to reflect usage leading up to the last few days.

Citations are the number of other articles citing this article, calculated by Crossref and updated daily. Find more information about Crossref citation counts.

The Altmetric Attention Score is a quantitative measure of the attention that a research article has received online. Clicking on the donut icon will load a page at altmetric.com with additional details about the score and the social media presence for the given article. Find more information on the Altmetric Attention Score and how the score is calculated.

  • Abstract

    Figure 1

    Figure 1. (a) Crystal structure of NiHCF, which has interstitial sites and vacancy sites. (b) Photograph of NiHCF granules.

    Figure 2

    Figure 2. Experimental setup of the NH3 adsorption and desorption. MFC stands for the mass flow controller. The adsorption and desorption lines are shown as red solid lines with closed arrows, and blue thin lines with open arrows, respectively. The thicker lines and the thinner lines represent gas and liquid lines, respectively. Pn and Fn represent the pressure and flow meter, respectively.

    Figure 3

    Figure 3. NH3 adsorption isotherms of NiHCF powder at 25 °C. The blue broken line indicates the partial pressure of NH3 in the inlet gas.

    Figure 4

    Figure 4. Results of NH3 adsorption and desorption. (a) NH3 concentration of the gas flow getting in/out of the NiHCF adsorbent in the three cycles of adsorption, which have a desorption step after the adsorption. (b) Ammonium nitrogen concentration (blue square) and pH (orange cross) in the washing liquid during desorption.

    Figure 5

    Figure 5. (a) Washed precipitate obtained after desorption. (b) FTIR spectra of the obtained precipitate and commercial NH4HCO3.

    Figure 6

    Figure 6. Adsorbed and desorbed NH3 amounts in each cycle. Red bars: adsorbed amount of NH3. blue bars: desorbed amount of NH3. The 2nd set of 3 cycles of the adsorption and desorption experiment was conducted in the same way as the 1st set (Figure 4) after changing the washing liquid used in the 1st set to a new one. The right axis exhibits the NH3 amount normalized by the adsorbent weight. The broken and dotted lines are the adsorbed and desorbed amounts in the reported batch experiment in the case of NiHCF, respectively. (29)

    Figure 7

    Figure 7. Material balance of NH3 species during the process of adsorption, desorption, and precipitation in cycle 3 of the 2nd set. The units of the numbers is mmol.

  • References


    This article references 35 other publications.

    1. 1
      U.S. Geological Survey. Nitrogen (Fixed)─Ammonia Miner. Commod. Summ. 2022.
    2. 2
      Boerner, L. K. Industrial Ammonia Production Emits More CO2 than Any Other Chemical-Making Reaction. Chemists Want to Change That Chem. Eng. News 2019, 97(24), https://cen.acs.org/environment/green-chemistry/Industrial-ammonia-production-emits-CO2/97/i24
    3. 3
      Krupa, S. Effects of Atmospheric Ammonia (NH3) on Terrestrial Vegetation: A Review. Environ. Pollut. 2003, 124 (2), 179221,  DOI: 10.1016/S0269-7491(02)00434-7
    4. 4
      Pitcairn, C. E. R.; Leith, I. D.; Sheppard, L. J.; Sutton, M. A.; Fowler, D.; Munro, R. C.; Tang, S.; Wilson, D. The Relationship between Nitrogen Deposition, Species Composition and Foliar Nitrogen Concentrations in Woodland Flora in the Vicinity of Livestock Farms. Environ. Pollut. 1998, 102 (1), 4148,  DOI: 10.1016/S0269-7491(98)80013-4
    5. 5
      Sheppard, L. J.; Leith, I. D.; Crossley, A.; Van Dijk, N.; Fowler, D.; Sutton, M. A.; Woods, C. Stress Responses of Calluna Vulgaris to Reduced and Oxidised N Applied under “Real World Conditions.. Environ. Pollut. 2008, 154 (3), 404413,  DOI: 10.1016/j.envpol.2007.10.040
    6. 6
      van den Berg, L. J. L.; Peters, C. J. H.; Ashmore, M. R.; Roelofs, J. G. M. Reduced Nitrogen Has a Greater Effect than Oxidised Nitrogen on Dry Heathland Vegetation. Environ. Pollut. 2008, 154 (3), 359369,  DOI: 10.1016/j.envpol.2007.11.027
    7. 7
      Nutrient Reduction Technology Cost Estimations for Point Sources in the Chesapeake Bay Watershed Prepared by The Nutrient Reduction Technology Cost Task Force A Stakeholder Group of the Chesapeake Bay Program November 2002 , 2002. https://www.chesapeakebay.net/content/publications/cbp_13140.pdf.
    8. 8
      Mladenović, M.; Paprika, M.; Marinković, A. Denitrification Techniques for Biomass Combustion. Renew. Sustain. Energy Rev. 2018, 82, 33503364,  DOI: 10.1016/j.rser.2017.10.054
    9. 9
      Melse, R. W.; Ogink, N. W. M. Air Scrubbing Techniques for Ammonia and Odor Reduction at Livestock Operations: Review of on-Farm Research in the Netherlands. Trans. Am. Soc. Agric. Eng. 2005, 48 (6), 23032313,  DOI: 10.13031/2013.20094
    10. 10
      Maurer, D. L.; Koziel, J. A. On-Farm Pilot-Scale Testing of Black Ultraviolet Light and Photocatalytic Coating for Mitigation of Odor, Odorous VOCs, and Greenhouse Gases. Chemosphere 2019, 221, 778784,  DOI: 10.1016/j.chemosphere.2019.01.086
    11. 11
      Li, G.; Kanezashi, M.; Yoshioka, T.; Tsuru, T. Ammonia Decomposition in Catalytic Membrane Reactors: Simulation and Experimental Studies. AIChE J. 2013, 59 (1), 168179,  DOI: 10.1002/aic.13794
    12. 12
      Lamb, K. E.; Dolan, M. D.; Kennedy, D. F. Ammonia for Hydrogen Storage; A Review of Catalytic Ammonia Decomposition and Hydrogen Separation and Purification. Int. J. Hydrogen Energy 2019, 44 (7), 35803593,  DOI: 10.1016/j.ijhydene.2018.12.024
    13. 13
      Yin, S. F.; Xu, B. Q.; Zhou, X. P.; Au, C. T. A Mini-Review on Ammonia Decomposition Catalysts for on-Site Generation of Hydrogen for Fuel Cell Applications. Appl. Catal. A Gen. 2004, 277 (1–2), 19,  DOI: 10.1016/j.apcata.2004.09.020
    14. 14
      Bist, R. B.; Subedi, S.; Chai, L.; Yang, X. Ammonia Emissions, Impacts, and Mitigation Strategies for Poultry Production: A Critical Review. J. Environ. Manage. 2023, 328, 116919  DOI: 10.1016/j.jenvman.2022.116919
    15. 15
      Chen, L.; Hoff, S. J.; Koziel, J. A.; Cai, L.; Zelle, B.; Sun, G. Performance Evaluation of a Wood-Chip Based Biofilter Using Solid-Phase Microextraction and Gas Chromatography-Mass Spectroscopy-Olfactometry. Bioresour. Technol. 2008, 99 (16), 77677780,  DOI: 10.1016/j.biortech.2008.01.085
    16. 16
      Chen, L.; Hoff, S.; Cai, L.; Koziel, J.; Zelle, B. Evaluation of Wood Chip-Based Biofilters to Reduce Odor, Hydrogen Sulfide, and Ammonia from Swine Barn Ventilation Air. J. Air Waste Manag. Assoc. 2009, 59 (5), 520530,  DOI: 10.3155/1047-3289.59.5.520
    17. 17
      Peng, F.; Gao, Y.; Zhu, X.; Pang, Q.; Wang, L.; Xu, W.; Yu, J.; Gao, P.; Huang, J.; Cui, Y. Removal of High-Strength Ammonia Nitrogen in Biofilters: Nitrifying Bacterial Community Compositions and Their Effects on Nitrogen Transformation. Water 2020, 12 (3), 712,  DOI: 10.3390/w12030712
    18. 18
      Rieth, A. J.; Dincă, M. Controlled Gas Uptake in Metal–Organic Frameworks with Record Ammonia Sorption. J. Am. Chem. Soc. 2018, 140 (9), 34613466,  DOI: 10.1021/jacs.8b00313
    19. 19
      Takahashi, A.; Tanaka, H.; Parajuli, D.; Nakamura, T.; Minami, K.; Sugiyama, Y.; Hakuta, Y.; Ohkoshi, S.; Kawamoto, T. Historical Pigment Exhibiting Ammonia Gas Capture beyond Standard Adsorbents with Adsorption Sites of Two Kinds. J. Am. Chem. Soc. 2016, 138 (20), 63766379,  DOI: 10.1021/jacs.6b02721
    20. 20
      Van Humbeck, J. F.; McDonald, T. M.; Jing, X.; Wiers, B. M.; Zhu, G.; Long, J. R. Ammonia Capture in Porous Organic Polymers Densely Functionalized with Bro̷nsted Acid Groups. J. Am. Chem. Soc. 2014, 136 (6), 24322440,  DOI: 10.1021/ja4105478
    21. 21
      Welsh, F. S. Particle Characteristics of Prussian Blue in an Historical Oil Paint. J. Am. Inst. Conserv. 1988, 27 (2), 5563,  DOI: 10.1179/019713688806046292
    22. 22
      Loos-Neskovic, C.; Dierkes, M. H. H.; Jackwerth, E.; Fedoroff, M.; Garnier, E. Fixation of Palladium on Insoluble Simple or Complex Cyano Compounds. Hydrometallurgy 1993, 32 (3), 345363,  DOI: 10.1016/0304-386X(93)90046-G
    23. 23
      Manakasettharn, S.; Takahashi, A.; Kawamoto, T.; Noda, K.; Sugiyama, Y.; Nakamura, T. Differences in NH3 Gas Adsorption Behaviors of Metal-Hexacyanoferrate Nanoparticles (M [FeII(CN)6] ·zH2O: M = In3+, Fe3+, and Mn2+). J. Solid State Chem. 2019, 270, 112117,  DOI: 10.1016/j.jssc.2018.10.026
    24. 24
      Parajuli, D.; Kitajima, A.; Takahashi, A.; Tanaka, H.; Ogawa, H.; Hakuta, Y.; Yoshino, K.; Funahashi, T.; Yamaguchi, M.; Osada, M.; Kawamoto, T. Application of Prussian Blue Nanoparticles for the Radioactive Cs Decontamination in Fukushima Region. J. Environ. Radioact. 2016, 151, 233237,  DOI: 10.1016/j.jenvrad.2015.10.014
    25. 25
      Takahashi, A.; Minami, K.; Noda, K.; Sakurai, K.; Kawamoto, T. Trace Ammonia Removal from Air by Selective Adsorbents Reusable with Water. ACS Appl. Mater. Interfaces 2020, 12 (13), 1511515119,  DOI: 10.1021/acsami.9b22384
    26. 26
      Usuda, H.; Sakurai, K.; Takahashi, A.; Kawamoto, T.; Minami, K. Ammonium Salt Production in NH3-CO2-H2O System Using a Highly Selective Adsorbent, Copper Hexacyanoferrate. Environ. Pollut. 2021, 288 (June), 117763  DOI: 10.1016/j.envpol.2021.117763
    27. 27
      Takahashi, A.; Minami, K.; Noda, K.; Sakurai, K.; Kawamoto, T. Harvesting a Solid Fertilizer Directly from Fetid Air. ACS Sustainable Chem. Eng. 2021, 9 (50), 1686516869,  DOI: 10.1021/acssuschemeng.1c06161
    28. 28
      Minami, K.; Takahashi, A.; Sakurai, K.; Mikasa, H.; Takasaki, M.; Doshu, N.; Aoyama, K.; Nakamura, T.; Iwai, R.; Kawamoto, T. Apparatus for Ammonia Removal in Livestock Farms Based on Copper Hexacyanoferrate Granules. Biosyst. Eng. 2022, 216, 98107,  DOI: 10.1016/j.biosystemseng.2022.02.002
    29. 29
      Usuda, H.; Mishima, Y.; Kawamoto, T.; Minami, K. Desorption of Ammonia Adsorbed on Prussian Blue Analogs by Washing with Saturated Ammonium Hydrogen Carbonate Solution. Mol. 2022, 27 (24), 8840,  DOI: 10.3390/molecules27248840
    30. 30
      Wessells, C. D.; Peddada, S. V.; Huggins, R. A.; Cui, Y. Nickel Hexacyanoferrate Nanoparticle Electrodes For Aqueous Sodium and Potassium Ion Batteries. Nano Lett. 2011, 11 (12), 54215425,  DOI: 10.1021/nl203193q
    31. 31
      Shrivastava, A.; Liu, S.; Smith, K. C. Linking Capacity Loss and Retention of Nickel Hexacyanoferrate to a Two-Site Intercalation Mechanism for Aqueous Mg 2+ and Ca 2+ Ions †. Phys. Chem. Chem. Phys. 2019, 21, 2017720188,  DOI: 10.1039/C9CP04115J
    32. 32
      Hall, H. K. Correlation of the Base Strengths of Amines. J. Am. Chem. Soc. 1957, 79 (20), 54415444,  DOI: 10.1021/ja01577a030
    33. 33
      National Astronomical Observatory of Japan. Handbook of Scientific Tables; Maruzen Publishing Co., Ltd., 2012.
    34. 34
      Khanna, R. K.; Moore, M. H. Carbamic Acid: Molecular Structure and IR Spectra. Spectrochim. Acta A Mol. Biomol. Spectrosc. 1999, 55 (5), 961967,  DOI: 10.1016/S1386-1425(98)00228-5
    35. 35
      Tao, W.; Ukwuani, A. T. Coupling Thermal Stripping and Acid Absorption for Ammonia Recovery from Dairy Manure: Ammonia Volatilization Kinetics and Effects of Temperature, PH and Dissolved Solids Content. Chem. Eng. J. 2015, 280, 188196,  DOI: 10.1016/j.cej.2015.05.119
  • Supporting Information

    Supporting Information


    The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acssuschemeng.3c05679.

    • Experimental setup of NH3 adsorption and desorption; additional results of characterization of the NiHCF adsorbent; and CO2 concentration in the outlet gas during adsorption (PDF)


    Terms & Conditions

    Most electronic Supporting Information files are available without a subscription to ACS Web Editions. Such files may be downloaded by article for research use (if there is a public use license linked to the relevant article, that license may permit other uses). Permission may be obtained from ACS for other uses through requests via the RightsLink permission system: http://pubs.acs.org/page/copyright/permissions.html.