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Analysis of Combustion By-products from Nitrogen-containing Organics in Regenerative Thermal Oxidizer
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Analysis of Combustion By-products from Nitrogen-containing Organics in Regenerative Thermal Oxidizer

2026-01-09

Author: Environmental Process Engineering Team
Date: November 26, 2025
Category: Industrial Emissions Control, RTO Technology

Introduction
With the growing demand for industrial waste gas treatment, Regenerative Thermal Oxidizers (RTOs) are widely used for treating Volatile Organic Compounds (VOCs) due to their high energy recovery efficiency and stable pollutant removal performance. However, when waste gases contain nitrogen-containing organic compounds (such as amines and nitro compounds), their combustion process may produce nitrogen oxides (NOx). Therefore, systematically analyzing the product composition and formation mechanisms of nitrogen-containing organic compounds in RTO combustion is crucial for optimizing process parameters, controlling secondary pollution, and complying with environmental regulations. The core of this analysis lies in understanding how different functional groups (such as amino, nitro groups, etc.) govern the chemical reaction pathways of nitrogen-containing molecules.

1. Mechanisms of Nitrogen Oxide Formation
The production of nitrogen oxides occurs through the following three pathways:
1. Thermal NOx: Formed by the oxidation of atmospheric nitrogen at high temperatures (above 1400°C), accounting for 15%–25% of total NOx generation.
2. Prompt NOx: Generated through the reaction of CH radicals (produced from high-temperature decomposition of hydrocarbons in fuel volatiles) with atmospheric nitrogen to form HCN and N, which then rapidly react with oxygen to produce NOx. This typically accounts for less than 5% of total NOx generation.
3. Fuel NOx: NOx generated from the oxidation of nitrogen-containing compounds in the fuel during combustion. Its formation is directly related to the structure of nitrogen-containing functional groups in the organic compounds, with significant differences in reactivity and conversion pathways among different nitrogen-containing functional groups.

图片1.png
As shown in the figure above, fuel-type NOx dominates nitrogen oxide emissions.

2. Factors Influencing NOx Generation
The combustion products of nitrogen-containing organic compounds are a mixture of N₂ and NOx. The NOx content is determined by various factors, including temperature, concentrations of N and O, fuel characteristics (particularly the type of nitrogen-containing functional groups), and residence time.
When the fuel gas contains nitrogen-containing components such as HCN, pyridine, or quinoline, the nitrogen in these compounds is first converted to HCN in the flame during combustion, then to NH or NH₂. This conversion process strongly depends on the nature of the initial nitrogen-containing functional groups. NH and NH₂ can react with oxygen to form NO + H₂O (e.g., 2NH₂ + 2O₂ → NO + 2H₂O) or react with NO to form N₂ + H₂O. In the flame, the proportion of fuel nitrogen converted to NO depends on the NO/O₂ ratio. When α is less than 0.7, almost no fuel-type NO is generated. Experiments show that 20%–80% of the nitrogen components in the fuel are converted to NO during combustion. If the oxygen supply during combustion is insufficient (α < 1), already formed NO can be partially reduced to N₂, lowering the NO content in the exhaust gas.
From the above description, the following conclusions can be drawn:
1. Higher combustion temperatures facilitate NOx formation. It is recommended to control the combustion temperature when burning nitrogen-containing organic compounds.
2. Higher oxygen content during combustion promotes NOx formation. Additionally, if the nitrogen-containing organic compound itself contains oxygen in its functional groups (e.g., -NO₂ in nitro compounds), it provides additional reactive oxygen atoms or promotes an oxidizing environment, thereby increasing the tendency for NOx generation.
3. During the combustion of nitrogen-containing organic compounds, they are first converted to HCN, then to NH or NH₂, which react with oxygen to form NOx. Therefore, there are systematic differences in the final NOx production due to different nitrogen-containing functional groups. Generally, compounds with amino functional groups (-NH or -NH₂) > cyanide functional groups (-CN).

3. Analysis of Combustion Products of Selected Nitrogen-Containing Organic Compounds

图片2.png
The conversion rates of several nitrogen-containing organic compounds to NOx can be calculated from the figure above.

1

Nitrobenzene

C₆H₅NO₂

Nitro (-NO₂)

1290

1.29

1664.1

800

1490

89.54

2

2-Nitrotoluene

C₇H₇NO₂

Nitro (-NO₂)

750

1.29

967.5

800

500

51.68

3

Aniline

C₆H₇N

Amino (-NH₂)

1340

1.29

1728.6

800

280

16.20

4

Aniline

C₆H₇N

Amino (-NH₂)

1340

1.29

1728.6

850

380

21.98

5

Propylamine

C₃H₉N

Amino (-NH₂)

1750

1.29

2257.5

800

270

11.96

6

Acrylonitrile

C₃H₃N

Cyano (-CN)

1700

1.29

2193

800

240

10.94

7

Butylamine

C₄H₁₁N

Amino (-NH₂)

1230

1.29

1586.7

800

130

8.19

8

Butylamine

C₄H₁₁N

Amino (-NH₂)

1230

1.29

1586.7

850

200

12.60

9

DMF

C₃H₇NO

Amide (-CON(CH₃)₂)

4600

1.29

5934

800

70

1.18

10

DMF

C₃H₇NO

Amide (-CON(CH₃)₂)

4600

1.29

5934

850

220

3.71

11

DMF

C₃H₇NO

Amide (-CON(CH₃)₂)

4600

1.29

5934

900

500

8.43

12

NH₃

NH₃

Amino (considered as -NH₃)

5800

1.29

7482

800

60

0.80

13

NH₃

NH₃

Amino (considered as -NH₃)

5800

1.29

7482

850

200

2.67

14

NH₃

NH₃

Amino (considered as -NH₃)

5800

1.29

7482

900

375

5.01

Note: DMF (Dimethylformamide) contains an amide functional group, which has relatively poor thermal stability. It decomposes at 350°C into CO and dimethylamine, and the latter burns to produce NOx. Therefore, DMF's conversion rate is lower than that of compounds directly bearing amino functional groups. Similarly, dimethylacetamide decomposes into CO and trimethylamine upon heating, and its conversion rate can be inferred analogously.
From the table above, the following conclusions can be drawn:
1.As the temperature increases, the slope of the conversion rate increases. Higher temperatures lead to more thermal NOx.
2.Influence of functional groups and molecular structure: Among compounds with similar nitrogen-containing functional groups, longer molecular chains and more substituents generally lead to lower conversion rates due to changes in steric hindrance and molecular stability. This may be because complex structures are more prone to fragmentation and reactions with hydrocarbon parts during combustion, reducing the likelihood of nitrogen atoms (from the functional groups) directly combining with oxygen to form NOx.
3.Effect of oxygen within the functional group: Compounds with functional groups containing both nitrogen and oxygen (e.g., nitro groups, as in nitrobenzene) show significantly higher conversion rates. This indicates that the elemental composition of the functional group itself is a key intrinsic factor influencing the nitrogen conversion pathway and efficiency.

Key Takeaways
Functional groups are predictive: The type of nitrogen-containing functional group in an organic compound is a primary determinant of its NOx conversion behavior in RTO systems.
Temperature control is critical: While functional groups dictate intrinsic reactivity, combustion temperature remains a powerful external lever for managing NOx emissions.
Structure matters: Beyond the core functional group, the broader molecular structure (chain length, substituents) modulates the conversion efficiency.
Oxygen in the group amplifies risk: Functional groups that incorporate oxygen atoms (like nitro groups) present a higher inherent NOx formation risk and warrant closer operational attention.