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1. 北京京能能源技术研究有限责任公司
2. 西安交通大学热流科学与工程教育部重点实验室
3. 京能盛乐热电有限公司
4. 北京能源集团有限责任公司
纸质出版:2026
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殷永江, 陈亮, 刘兴, 等. 350MW燃煤机组混燃压块牛粪试验研究[J]. 热力发电, 2026,(10).
殷永江, 陈亮, 刘兴, et al. 350MW燃煤机组混燃压块牛粪试验研究[J]. Thermal Power Generation, 2026, (10).
殷永江, 陈亮, 刘兴, 等. 350MW燃煤机组混燃压块牛粪试验研究[J]. 热力发电, 2026,(10). DOI: 10.19666/j.rlfd.202601061.
殷永江, 陈亮, 刘兴, et al. 350MW燃煤机组混燃压块牛粪试验研究[J]. Thermal Power Generation, 2026, (10). DOI: 10.19666/j.rlfd.202601061.
【目的】为响应煤电低碳化改造政策,同时解决北方畜牧业牛粪污染及资源浪费难题,开展了燃煤机组掺烧压块牛粪可行性试验。【方法】基于内蒙古某350 MW机组,在未对原有设备改造的前提下,采用“单磨掺烧”共磨技术,在0~20%掺烧工况下,系统研究了掺烧对制粉系统适应性、锅炉燃烧特性、污染物排放特性及除尘系统的影响。【结果】掺烧比例超过10%~15%时,磨煤机电流、单位功耗、前后压差变化明显,最大增幅分别为3.96 A、0.64 kW·h/t、0.59 kPa;且燃料细度降低,R
200
、R
90
最大增量分别为1.95%、6.53%。掺烧后,锅炉燃烧状况良好,炉膛温度、排烟温度的波动较小;CO质量浓度稳定在60.00 mg/m
3
附近;灰渣中含碳量变化不明显;锅炉效率略降,最大降低率为0.19百分点,掺烧对污染物排放及除尘系统无明显影响。掺烧压块牛粪后,NO
x
生成量略微上升;SO
2
降低幅度较小;电袋除尘运行参数稳定,布袋除尘前后压差无明显变化。【结论】研究结果表明,利用机组现有设备可实现牛粪的高效掺烧,为畜禽粪污的资源化利用提供了可复制、可推广的技术新模式。
[Objective
]
To align with the national policy on low-carbon retrofitting of coal-fired power plants and tackle the dual challenges of cow dung pollution and underutilization of this resource in the animal husbandry sector of northern China
this study carried out a test on briquetted cow dung co-combustion in coal-fired power units
to explore a low-cost
easy-to-implement technical solution for both coal power decarbonization and livestock manure resource utilization. [Methods
]
This study selected a 350 MW coal-fired power plant in Inner Mongolia as the research subject and conducted briquetted cow dung co-combustion experiments adopting the “single-mill cofiring” technology
with no retrofitting required for the existing equipment. Under co-firing ratios
of 0~20%
this study systematically investigated the effects of co-combustion on the adaptability of the pulverizing system
combustion characteristics of the boiler
pollutant emission characteristics
and performance of the dust removal system. [Results
]
The results show that when the co-firing ratio exceeds the range of 10%~15%
the mill current
specific power consumption
and pressure difference across the mill exhibit significant variations
with a maximum increments of 3.96 A
0.64 kW·h/t
and 0.59 k Pa
respectively. Furthermore
the fineness of pulverized coal decreases
with the two screen residue indices(R
200
and R
90
) registering maximum increments of 1.95% and 6.53%
respectively. After co-firing briquetted cow dung
the boiler maintains stable combustion performance
with only slight fluctuations observed in furnace and flue gas temperatures. The CO mass concentration remains stable at 60.00 mg/m
3
the carbon content of ash shows negligible variations
and boiler thermal efficiency undergoes a marginal decline with a maximum reduction rate of 0.19 percentage point. This co-firing technology exerts no significant influence on pollutant emissions and the operating parameters of the dust removal system. Under the pure coal combustion condition
the NO
x
mass concentration at the SCR inlet is 264.86 mg/m
3
and the SO
2
mass concentration at the desulfurization inlet is 2 771.38 mg/m
3
. After co-firing
NO
x
generation shows a slight increase with a growth rate ranging from 3.94% to 8.19%(equivalent to an absolute increment of 10.45~21.69 mg/m
3
); SO
2
mass emissions experience a minimal reduction and remain essentially stable. Meanwhile
the current and voltage parameters of the electrostatic precipitator stay relatively stable
and the pressure difference across the bag filter section presents no obvious variation
with a maximum increment of only 72.87 Pa. [Conclusion
]
The findings demonstrate that u
tilizing the existing equipment of the unit enables the efficient co-combustion of cow manure
offering a replicable and scalable new technical paradigm for the resource utilization of livestock and poultry manure waste.
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