...
首页> 外文期刊>The International Journal of Life Cycle Assessment >Life cycle inventory of energy production in ArcelorMittal steel power plant Poland S.A. in Krakow, Poland
【24h】

Life cycle inventory of energy production in ArcelorMittal steel power plant Poland S.A. in Krakow, Poland

机译:波兰克拉科夫的ArcelorMittal钢铁厂Poland S.A.的能源生产生命周期清单

获取原文
获取原文并翻译 | 示例
           

摘要

Purpose The goal of this paper is to describe the life cycle inventory (LCI) approach of energy produced by ArcelorMittal Steel Power Plant Poland (AMSPPP) in Krakow, Poland. The present LCI is representative for the reference year 2005 by application of ISO 14040: 2006. The system boundaries were labeled as gate-to-gate (it covered full process chain for energy production). Background data of inputs and outputs from the steel power plant have been inventoried as follows: consump tion of energy and fuels, including: power coal (domestic), natural gas, blast furnace gas and coke oven gas, emission of air pollutants, emissions of particulate, air emissions from stockpiles, wastes, internal transport, and land use. Main feature LCI energy generation was developed mainly on the basis of following sources: site-specific measured or calculated data, life cycle assessment (LCA) study carried out by Polish Academy of Science in Krakow, AMSPPP Environmental Impact Report, Company and literature information and expert consultations. The functional unit is represented by 977 MW of generated electric and heat energies, distributed to ArcelorMittal Steel Plant processes and to the Krakow's grid. Time coverage is 2005. Operating parameters as well as air emissions associated with the power plant boilers were presented. The production data (steams: 9, 1.6, and 0.8 MPa, electric energy, degassing softening water, softening water heat, and blast furnace blow) were given. The emissions of SO_2, NO_X, CO, CH_4, HC1, dust, heavy metals (Cr, Cd, Cu, Pb, Ni, and Mn), pollution factors (BOD_5, COD) of waste water released from ash, slag, and sludge disposals were estimated. Finally, emission of CO_2 was calculated. Continuous monitoring of air pollutant emissions conducted in two emitter units related to 977 MW energy produced in AMSPPP was discussed. Results and discussion Related to 977 MW of energy production distributed by AMSPPP, the consumption of blast furnace gas, coke oven gas, and natural gas were 1,279.7, 47,441, and 2,080 Mm~3/year, respectively. Other fuel consumption, power coal (domestic), was 315,680 Mg/year. The production data of steams: 9, 1.6, and 0.8 MPa were estimated at 3,689,640; 227,642; and 335,010 Mg, respec tively. The volume of heat was about 1,529,610 GJ. Degassing softening water and softening water represented 1,066,674 and 2,124,466 m~3. Electric energy amount was on the order 441,188 MWh, and resulting value of the blast furnace blow was 3,076,606,000 m~3. Nominal powers of the power plant boilers ranged from 149 to 177 MW. Direct dust, SO_2, NO_2, and CO emissions into the air from seven boilers (Nos. 1-7) were 33, 159.9, 134, and 8 kg/h, and from boiler No. 8 (coal-only) were 17.70, 222.6, 112, and 1.11 kg/h, respectively. Total CO_2 emission was 1,802,902 Mg. Direct CO_2 emissions from burning of power coal, blast furnace gas, coke oven gas, and finally natural gas were 674,317, 1,084,797, 39,802, and 3,986 Mg, respectively. The amounts of SO_2, NO_x (expressed as NO_2 eq.) CO, CH_4, HC1 and dust emissions were 3,138.1, 2,648.5, 48.1, 575.08, 117.2, and 622.1 Mg, respectively. Contents of Mg, Cr, Cd, Cu, Pb, Ni, Mn in ash were on the order of 19.4, 1.8, 60, 50, 45, and 475 mg/kg, respectively (max. values, 28.4, 2.3, 75, 68, 59, 682, respectively). COD and BOD_5 ranged 1.2 to 17 and 10.9 to 42.7 mg O_2/dm~3, respectively. Contribution of power coal stockpiles to heavy metal emissions was relatively small. The amounts of ash-sludge mixtures and carbon volatile ash during stock of power coal were 53,078.1 and 11,272 Mg, respectively. Data concerning pollutants into air from continuous monitoring were not included due to a limitation of the available data. The time coverage of the data collected from continuous monitoring is 2006. Conclusions This is the first tentative study to express energy generation in industry in Poland in terms of LCA/LCI for the energy power in steel industry. The results of the study suggest that reduction of the amount of power coal leads to saving of primary resources and reduction of SO_2 emissions, decrease land occupation caused by power coal stockpiles, and increase recovery of the blast furnace gas, as well as, coke oven gas surplus. The results may help ArcelorMittal Steel Plant government make decisions in policy making. Presen tation of the study in this paper is suitable for the energy production processes, as well as other industries. Recommendations and outlook The LCI offers environ mental information consisting on the list of environmental loads. The impact assessment phase aims the results from the inventory analysis to be more understandable and life cycle impact assessment will be the direction for future research. Another issue to discuss is integration of LCA and risk assessment for industrial processes.
机译:目的本文的目的是描述波兰克拉科夫的安赛乐米塔尔钢铁电厂(AMSPPP)生产的能源的生命周期清单(LCI)方法。当前的LCI通过应用ISO 14040:2006代表2005基准年。系统边界标记为“门到门”(涵盖了能源生产的整个过程链)。钢铁电厂的投入和产出的背景数据按以下方式盘存:能源和燃料的消耗,包括:动力煤(家用),天然气,高炉煤气和炼焦炉煤气,空气污染物的排放,微粒,库存产生的空气排放,废物,内部运输和土地使用。 LCI能源生产的主要特征主要是基于以下来源开发的:特定地点的测量或计算数据,波兰科学院在克拉科夫进行的生命周期评估(LCA)研究,AMSPPP环境影响报告,公司和文献信息以及专家咨询。该功能单元由977 MW的发电和热能代表,分配给阿塞洛米塔尔钢铁厂的工艺和克拉科夫的电网。时间范围是2005年。介绍了运行参数以及与电厂锅炉相关的空气排放。给出了生产数据(蒸汽:9、1.6和0.8 MPa,电能,软化水脱气,软化水热和高炉吹气)。灰分,矿渣和污泥释放的废水中的SO_2,NO_X,CO,CH_4,HCl,粉尘,重金属(Cr,Cd,Cu,Pb,Ni和Mn)的排放,污染因子(BOD_5,COD)估计处置量。最后,计算了CO_2的排放量。讨论了在两个与AMSPPP中产生的977兆瓦能源有关的排放单位中进行的空气污染物排放的连续监测。结果与讨论与AMSPPP分配的977 MW能源生产相关,高炉煤气,焦炉煤气和天然气的消耗分别为每年1,279.7、47,441和2,080 Mm〜3 /年。动力煤(家用)的其他燃料消耗为315,680 Mg /年。蒸汽的生产数据:9、1.6和0.8 MPa估计为3,689,640; 227,642;和335,010 Mg。热量约为1,529,610 GJ。脱气软化水和软化水分别为1,066,674和2,124,466 m〜3。电能数量为441,188 MWh,高炉吹气的总值为3,076,606,000 m〜3。电厂锅炉的额定功率范围为149到177兆瓦。七个锅炉(1-7号)向空气中的直接粉尘,SO_2,NO_2和一氧化碳排放量分别为33、159.9、134和8 kg / h,而8号锅炉(仅煤)的直接粉尘排放量为17.70, 222.6、112和1.11 kg / h。 CO_2总排放量为1,802,902 Mg。动力煤,高炉煤气,焦炉煤气和最终天然气燃烧产生的直接CO_2排放分别为674,317、1,084,797、39,802和3,986 Mg。 SO_2,NO_x(以NO_2当量表示)CO,CH_4,HCl和粉尘排放量分别为3,138.1、2,648.5、48.1、575.08、117.2和622.1 Mg。灰分中Mg,Cr,Cd,Cu,Pb,Ni,Mn的含量分别为19.4、1.8、60、50、45和475 mg / kg的数量级(最大值,28.4、2.3、75,分别为68、59、682)。 COD和BOD_5分别为1.2〜17和10.9〜42.7 mg O_2 / dm〜3。动力煤库存对重金属排放的贡献相对较小。动力煤储存期间的灰渣混合物和碳挥发性灰分的量分别为53,078.1和11,272 Mg。由于现有数据的局限性,没有包括连续监测的空气污染物数据。连续监测收集的数据的时间覆盖范围是2006年。结论这是第一个以LCA / LCI表示钢铁工业能源的波兰工业能源产生的初步研究。研究结果表明,减少动力煤的数量可以节省主要资源并减少SO_2的排放,减少动力煤库存引起的土地占用,并提高高炉煤气和焦炉的回收率天然气过剩。结果可能有助于安赛乐米塔尔钢铁厂政府做出决策。本文的介绍适用于能源生产过程以及其他行业。建议和展望LCI提供了有关环境负荷清单的环境信息。影响评估阶段旨在使库存分析的结果更易于理解,生命周期影响评估将成为未来研究的方向。讨论的另一个问题是LCA与工业流程风险评估的集成。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号