Close Go back Collapse all sections
Process Data set: cement production;cement, ordinary portland cement, 42.5MPa;new dry process, low-temperature waste heat power generation technology, 2000 t/d;fly ash (en) en zh

Key Data Set Information
Location HLJ-CN
Geographical representativeness description Mudanjiang New Material Technology Co., Ltd.
Reference year 2008
Name
cement production;cement, ordinary portland cement, 42.5MPa;new dry process, low-temperature waste heat power generation technology, 2000 t/d;fly ash
Use advice for data set When utilizing this dataset for environmental impact assessments and life cycle analyses, LCA practitioners should closely consider the specific operating conditions detailed, such as temperatures and energy outputs. Attention should be paid to the implications of energy- and resource-efficiency improvements, integration of waste materials (fly ash and carbide slag), and emission reductions due to the waste heat recovery system. It's important to note that clay resource consumption and the environmental impact of iron powder correction materials are excluded from this data. Emission data for NOx, SO2, CO2, and dust at the output end should be taken into account.
Technical purpose of product or process The cement production process described is used in the manufacturing of ordinary Portland cement, with a specified compressive strength of 42.5MPa. This particular process applies new dry process technology integrated with a low-temperature waste heat power generation system capable of handling 2000 tons per day, which includes the use of fly ash and carbide slag, a by-product from the acetylene chemical industry in Heilongjiang. This approach serves to lower carbon emissions and improve environmental sustainability within the cement industry.
Classification
Class name : Hierarchy level
  • ILCD: Unit processes / Materials production / Other mineralic materials
General comment on data set Laboratory data. New dry process low temperature waste heat power generation.The cement is produced by burning carbide slag generated by the acetylene industry in Heilongjiang. The new dry production line for low-temperature waste heat power generation uses the exhaust gas waste heat from the cooler at the kiln head and the preheater at the kiln tail, which is about 350°C, as the heating energy source. The low-pressure backpressure steam turbine is used for low-temperature waste heat power generation. An AQC waste heat boiler (vertical structure) is installed between the kiln head cooler and the waste gas fan, with a settling chamber before the AQC boiler. An SP waste heat boiler is installed between the kiln tail rotary kiln outlet and the high-temperature fan.The AQC boiler adopts the middle section air extraction with recycled waste gas method, and the original waste gas extraction port is changed into two extraction ports, with one high-temperature extraction port located in the front and one low-temperature extraction port located in the rear. The high-temperature hot air from the front extraction port is recovered after some fly ash is collected in the settling chamber and sent to the AQC boiler, while the low-temperature extraction port is mixed with the AQC boiler outlet air and processed by the original cement production line dust removal system. The waste gas at the kiln tail is cooled and heated by the SP boiler to around 230°C, and a part of it is sent to the raw material mill of the original system by the high-temperature fan, while the other part is humidified in the humidification tower before being sent to the tail gas dust collector. If the power generation system stops operating, the waste gas enters the high-temperature fan through the waste gas pipeline of the original system to ensure the stable operation of the cement production line.Through heat exchange, the boiler produces superheated steam, which is sent to the mixed steam cylinder for mixing and then enters the steam turbine for power generation through the superheated steam pipeline. The low-pressure steam from the steam turbine enters the condenser, where the steam condenses into water, which flows into the hot water well and is then pumped into the vacuum deaerator by a water pump. The water is then pumped into the AQC boiler for circulation by the feedwater pump.
Copyright No
Owner of data set
Quantitative reference
Reference flow(s)
Technological representativeness
Technology description including background system This section selects the above process and uses calcium carbide slag produced by the Heilongjiang Yikuai chemical industry to burn cement to improve the environmental coordination of the Heilongjiang cement industry and promote the sustainable development of the cement industry. The process flow of pre-drying, dry grinding and dry burning is shown in Figure 5-1. Figure 5-4 shows the process flow of low-temperature waste heat power generation in the new dry process production line. This process uses about 350% flue gas waste heat discharged from the kiln head clinker cooler and kiln tail preheater as heating energy, and generates low-temperature waste heat power generation through a low-pressure steam turbine. An AQC waste heat boiler (vertical structure) is arranged between the kiln head cooler and the residual air fan, and a descending chamber is arranged in front of the AOC boiler; an SP waste heat boiler is installed between the outlet of the tail first-stage rotor and the high-temperature fan.The AQC boiler adopts the middle exhaust with residual air recirculation method. The original residual air exhaust outlet is changed to two exhaust outlets. One of the new exhaust outlets is moved to the front and the other is moved to the rear. The hot air from the front high-temperature exhaust outlet recovers part of the fly ash through the settling chamber. It is sent to the AOC boiler. The moved low-temperature exhaust air is mixed with the AOC boiler outlet air and then processed by the dust removal system of the original cement production line. The dense tail exhaust gas absorbs heat and is cooled to about 230C by the SP boiler. A part of the high temperature fan is sent to the raw meal mill of the original system, and the other part is humidified by the humidification tower and then sent to the tail dust collector. If the power generation system is disabled, the exhaust gas The exhaust gas pipe of the original system enters the high-temperature fan to ensure stable operation of the cement production line.Through heat energy exchange, the boiler generates superheated steam, which is sent to the separate cylinders for mixing, and then enters the steam turbine through the superheated steam pipe to generate electricity. The spent steam from the steam turbine enters the condenser. The spent steam condenses into water in the condenser and flows into the hot water well. It is then sent to the vacuum deaerator by the water pump, and then pumped into the AQC boiler through the feed water pump for recycling.
Flow diagram(s) or picture(s)
  • V7g3bWp8nofis5xNQlgc7xjbnuf.png Image
Mathematical model
Model description The functional unit is the performance of 1kg cement with a 28-day compressive strength of 42.5MPa, that is, 1Fu=42.5kgMPa. The scope of evaluation is raw meal preparation, clinker calcination and cement preparation. The environmental load caused by the consumption of clay resources is not considered for the time being. Iron powder is an iron correction material, and its environmental impact will not be considered. The wastes considered to be emitted at the output end of the product system mainly include nitrogen oxides, sulfur dioxide, carbon dioxide and dust.
LCI method and allocation
Type of data set Unit process, black box
Deviation from LCI method principle / explanations None
Deviation from modelling constants / explanations None
Data sources, treatment and representativeness
Deviation from data cut-off and completeness principles / explanations None
Data selection and combination principles Combined with the renovation design of Mudanjiang New Material Technology Co., Ltd.'s new dry process waste heat utilization energy-saving technology, the input and output data of the determined product system were collected, and the data were calculated and quantified.(1) Waste heat conditions can be utilized. 2 2000t/d new dry process production lines. In order to ensure the quality of waste heat, the inlet air of the waste heat furnace at the kiln head is extracted from the middle of the pavilion cooling machine. The air volume is 2x170329Nm^3/h, the exhaust gas temperature is 360°C, the waste heat utilization temperature range is 360~86°C, and the heat is 12302E+4kJ/h; the tail preheater The air intake volume of the heater is 2x203147Nm^3/h, and the exhaust gas temperature is 350°C. Considering the dry heat consumption of the coal mill, the waste heat utilization range is 350-205°C, with a heat capacity of 7927E+4kJ/h.(2) Installed capacity. Use the waste heat of the kiln tail waste gas to set up a kiln tail waste heat boiler. 2 kiln tail waste heat boilers can produce 2x13.5t/h-1.35Mpa-320 superheated steam; use the kiln head clinker cooler waste gas waste heat to set up a kiln head waste heat boiler. 2 The kiln head waste heat boiler can produce 2x9.0t/h-1.35Mpa-345 superheated steam and 62t/h-170 hot water at the same time, of which 44t/h is supplied to the kiln head and tail waste heat boilers to produce main steam, and 18t/h is supplied to the steam turbine. Room flash evaporation produces low-pressure saturated steam. According to the main steam quality that the waste heat boiler can produce, a steam-admission steam turbine is selected. The main steam parameter is 1.25MPa-320; the main steam volume produced by the head and tail is 45t/h, and the low-pressure steam volume produced by the head boiler is 5t/h. ; Calculated based on the overall efficiency of the steam turbine and generator being 805%, the average waste heat power generation power is 8600kW.(3) Save electricity. According to the actual operating conditions and power generation efficiency of the low-temperature waste heat power station, the average power generation power of the power station is 8600kW. Calculated based on the annual operation of 7200 hours, the annual power generation is 6192E+4kWh; deducting 7.8% of the power station’s self-consumption rate, which is 483E+4kWh, the actual power of the waste heat power station is 8600kW. The production line supplies 5709E+4kWh.(4) Reduce emissions. An interference separator is installed at the exhaust gas inlet of the waste heat boiler, which is conducive to the sedimentation of dust in the exhaust gas and reduces the dust content in the cement kiln exhaust gas by nearly 50%. Since thermal power generation is used in the north, electric energy is saved to reduce CO2 and SO2 caused by coal combustion during the power generation process. and NOx emissions.Through the above analysis, the inventory and analysis data of the environmental impact assessment of the cement industry under the new dry process low-temperature waste heat power generation scheme are calculated and obtained.
Deviation from data selection and combination principles / explanations None
Deviation from data treatment and extrapolations principles / explanations None
Data source(s) used for this data set
Completeness
Completeness of product model No statement
Validation
Type of review
Dependent internal review
Reviewer name and institution
Data generator
Data set generator / modeller
Data entry by
Time stamp (last saved) 2024-03-19T21:18:09+08:00
Publication and ownership
UUID aa6656f9-d94c-4d25-889d-cd675272b069
Date of last revision 2024-04-20T14:41:41.250354+08:00
Data set version 00.01.005
Permanent data set URI https://lcadata.tiangong.world/showProcess.xhtml?uuid=aa6656f9-d94c-4d25-889d-cd675272b069&version=01.00.000&stock=TianGong
Owner of data set
Copyright No
License type Free of charge for all users and uses

Inputs

Type of flow Classification Flow Location Mean amount Resulting amount Minimum amount Maximum amount
Product flow
Materials production / Other mineralic materials 1104.4 kg1104.4 kg
General comment Limestone
Product flow
Materials production / Other mineralic materials 58.7 kg58.7 kg
General comment Gypsum
Waste flow
Wastes 319.4 kg319.4 kg
General comment Fly ash
Product flow
Energy carriers and technologies / Hard coal based fuels 100.526 kg100.526 kg
General comment Standard coal. The original data is 0.0934kg standard coal, here converted to hard coal, the conversion formula is 1kg hard coal = 0.929kg standard coal.
Product flow
Energy carriers and technologies / Electricity 211.32000000000002 MJ211.32000000000002 MJ
General comment Electricity

Outputs

Type of flow Classification Flow Location Mean amount Resulting amount Minimum amount Maximum amount
Elementary flow
Emissions / Emissions to air / Emissions to air, unspecified 0.249 kg0.249 kg
General comment Dust
Elementary flow
Emissions / Emissions to air / Emissions to air, unspecified 0.3893 kg0.3893 kg
General comment Sulfur dioxide
Elementary flow
Emissions / Emissions to air / Emissions to air, unspecified 1.557 kg1.557 kg
General comment Nitrogen oxides
Elementary flow
Emissions / Emissions to air / Emissions to air, unspecified 813.1 kg813.1 kg
General comment Carbon dioxide
Product flow
Materials production / Other mineralic materials 1000.0 kg1000.0 kg
General comment 42.5 Ordinary silicate cement