The combustion behaviors of anthracite and dried sawmill sludge (DSS) were studied using thermogravimetric analysis (TGA) and derivative thermogravimetric analysis (DTG). DSS was found to be a promoter for anthracite combustion, the addition of DSS in anthracite decreased the burnout temperature and time. But DSS caused the rapid releases of SO₂ and NO in the initial combustion stage. In overall, the increasing of DSS significantly decreased the emission factor of SO₂ from 13.42 ± 1.80 to 0.31 ± 0.08 g/kg; while the emission factor of NO was not obviously changed and stable at 0.7–0.8 g/kg in all cases. The oxygen-rich atmosphere was helpful for the rapid and sufficient combustion of blend; the oxygen-lean atmosphere delayed the combustion process and slowed down the releases of SO₂ and NO. The increasing combustion temperature improved the anthracite combustion, and the emission factors of SO₂ and NO were all increased with the temperature increasing. 900 °C was found to be the best combustion temperature for NO generation. SO₃ was detected in the combustion of anthracite under 21% and 30% of O₂. Two promising ways for control of SO₂ and NO were provided: 1) urea-fuel mixture combustion combined with the post-combustion wet absorption by Na₂CO₃; 2) post-combustion wet absorption by NaClO/Na₂CO₃. The removal efficiencies of SO₂ and NO could reach 100% and over 95% respectively. The removal products were determined as sulfate, sulfite and nitrate by IC, with no toxic byproducts being produced.

利用热重分析（TGA）和衍生热重分析（DTG）研究了无烟煤和干锯木厂污泥（DSS）的燃烧行为。发现DSS是无烟煤燃烧的促进剂，在无烟煤中添加DSS降低了燃尽温度和时间。但是DSS在燃烧初期导致了SO ₂和NO的快速释放。总体而言，DSS的增加显着降低了SO ₂的排放因子从13.42±1.80到0.31±0.08 g / kg; 在所有情况下，NO的排放因子并没有明显变化，并且稳定在0.7-0.8 g / kg。富氧气氛有助于混合物快速充分地燃烧。贫氧气氛延迟了燃烧过程并减慢了SO ₂和NO的释放。燃烧温度的升高改善了无烟煤的燃烧，SO ₂和NO的排放因子均随温度的升高而增加。发现900°C是产生NO的最佳燃烧温度。在无烟煤燃烧过程中，在21％和30％的O ₂下检测到SO ₃。控制SO _2的两种有前途的方法并提供NO：1）尿素燃料混合物燃烧与Na ₂ CO ₃燃烧后湿吸收相结合；2）燃烧后通过NaClO / Na ₂ CO _3的湿吸收。SO ₂和NO的去除率分别达到100％和95％以上。通过离子色谱法将去除的产物确定为硫酸盐，亚硫酸盐和硝酸盐，没有产生有毒的副产物。