硅酸盐通报 ›› 2026, Vol. 45 ›› Issue (3): 1083-1093.DOI: 10.16552/j.cnki.issn1001-1625.2025.1124
刘晨宇1,2(
), 张文露1, 李从云1, 曾健华1, 李路瑶1(
), 韩建军1, 王静1
收稿日期:2025-11-14
修订日期:2026-01-12
出版日期:2026-03-20
发布日期:2026-04-10
通信作者:
李路瑶,博士,助理研究员。E-mail:liluyao91@whut.edu.cn作者简介:刘晨宇(2003—),男,硕士研究生。主要从事综合能源系统方面的研究。E-mail:cyliuu@foxmail.com
基金资助:
LIU Chenyu1,2(
), ZHANG Wenlu1, LI Congyun1, ZENG Jianhua1, LI Luyao1(
), HAN Jianjun1, WANG Jing1
Received:2025-11-14
Revised:2026-01-12
Published:2026-03-20
Online:2026-04-10
摘要:
玻璃熔制过程能耗高、碳排放量大,原料中碳酸盐的分解与燃料燃烧是主要碳排放来源。为探究从原料端减碳的可行途径,本文基于固定的目标氧化物组成,采用热重-差示扫描量热分析法结合高温熔融实验,研究传统配方、两种减碳配方及掺50%(质量分数)碎玻璃配方,共4组配方的反应热、熔化行为和CO2排放。结果表明,以硅酸钙替代传统原料中的碳酸钙并配合NaOH作为高效助熔剂的配方节能降碳协同效益最显著,理论总热耗较传统配方降低约21.1%,总CO2排放量减少65.4%。掺入50%碎玻璃可使熔化温度较传统配方降低50 ℃并减排37.1%,但减碳潜力受限于残余碳酸盐。若以硅酸盐代替碳酸盐而未配高效助熔剂,则因熔化温度升高导致能耗上升34.7%。研究表明,引入硅酸盐代替碳酸盐并加入高效助熔剂是玻璃工业源头减碳的有效途径,通过明确低碳原料体系对应的熔化温度与热耗水平,为原料配方设计及玻璃生产工艺制度优化提供了理论依据。
中图分类号:
刘晨宇, 张文露, 李从云, 曾健华, 李路瑶, 韩建军, 王静. 低碳玻璃配方对玻璃熔制过程及CO2排放的影响[J]. 硅酸盐通报, 2026, 45(3): 1083-1093.
LIU Chenyu, ZHANG Wenlu, LI Congyun, ZENG Jianhua, LI Luyao, HAN Jianjun, WANG Jing. Effect of Low-Carbon Glass Batch Formulations on Glass Melting Process and CO2 Emissions[J]. BULLETIN OF THE CHINESE CERAMIC SOCIETY, 2026, 45(3): 1083-1093.
| Oxide component | SiO2 | CaO | Al2O3 | Na2O | Li2O |
|---|---|---|---|---|---|
| Mass fraction/% | 73.9 | 7.6 | 2.6 | 15.8 | 0.2 |
表1 玻璃的目标氧化物组成
Table 1 Target oxide composition of glass
| Oxide component | SiO2 | CaO | Al2O3 | Na2O | Li2O |
|---|---|---|---|---|---|
| Mass fraction/% | 73.9 | 7.6 | 2.6 | 15.8 | 0.2 |
Formulation No. | Mass/g | Mass fraction/% | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| Na(AlSi3O8) | LiAl(Si2O6) | SiO2 | CaCO3 | CaSiO3 | Na2CO3 | Li2CO3 | Na2SiO3 | NaOH | Cullet | ||
| Ⅰ | 116.6 | 11.5 | — | 55.7 | 11.6 | — | 20.8 | 0.4 | — | — | — |
| Ⅱ | 104.2 | 10.0 | 2.0 | 55.0 | — | 15.0 | — | — | — | 18.0 | — |
| Ⅲ | 100.0 | 10.4 | 2.1 | 43.3 | — | 15.6 | — | — | 28.6 | — | — |
| Ⅳ | 107.5 | 5.7 | — | 27.8 | 5.8 | — | 10.5 | 0.2 | — | — | 50.0 |
表2 四组配方中各原料组分质量占比
Table 2 Mass fraction of raw material components in four batch formulations
Formulation No. | Mass/g | Mass fraction/% | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| Na(AlSi3O8) | LiAl(Si2O6) | SiO2 | CaCO3 | CaSiO3 | Na2CO3 | Li2CO3 | Na2SiO3 | NaOH | Cullet | ||
| Ⅰ | 116.6 | 11.5 | — | 55.7 | 11.6 | — | 20.8 | 0.4 | — | — | — |
| Ⅱ | 104.2 | 10.0 | 2.0 | 55.0 | — | 15.0 | — | — | — | 18.0 | — |
| Ⅲ | 100.0 | 10.4 | 2.1 | 43.3 | — | 15.6 | — | — | 28.6 | — | — |
| Ⅳ | 107.5 | 5.7 | — | 27.8 | 5.8 | — | 10.5 | 0.2 | — | — | 50.0 |
| Formulation No. | Predicted melting temperature range/℃ | Experimental set temperature/℃ |
|---|---|---|
| Ⅰ | 1 200~1 250 | 1 200, 1 225, 1 250 |
| Ⅱ | 1 200~1 250 | 1 200, 1 225, 1 250 |
| Ⅲ | 1 400~1 500 | 1 425, 1 450, 1 475 |
| Ⅳ | 1 150~1 200 | 1 175, 1 200, 1 225 |
表3 四组配方样品所设实验温度
Table 3 Experimental temperatures set of samples for four batch formulations
| Formulation No. | Predicted melting temperature range/℃ | Experimental set temperature/℃ |
|---|---|---|
| Ⅰ | 1 200~1 250 | 1 200, 1 225, 1 250 |
| Ⅱ | 1 200~1 250 | 1 200, 1 225, 1 250 |
| Ⅲ | 1 400~1 500 | 1 425, 1 450, 1 475 |
| Ⅳ | 1 150~1 200 | 1 175, 1 200, 1 225 |
| Formulation No. | Peak | Peak temperature/℃ | Onset temperature/℃ | End temperature/℃ | Peak area/(J·g-1) |
|---|---|---|---|---|---|
| Ⅰ | a | 132.3 | 112.5 | 147.0 | -13.8 |
| b | 573.8 | 569.2 | 578.6 | -4.6 | |
| c | 685.9 | 618.1 | 710.7 | -431.0 | |
| d | 815.9 | 806.5 | 828.6 | -58.0 | |
| e | 844.6 | 838.9 | 850.9 | -13.9 | |
| Ⅱ | a | 92.8 | 40.7 | 136.7 | -261.9 |
| b | 268.8 | 254.7 | 283.5 | -7.9 | |
| c | 424.7 | 390.1 | 440.2 | -16.8 | |
| d | 573.5 | 569.2 | 579.3 | -4.2 | |
| e | 914.9 | 898.9 | 936.3 | 15.9 | |
| Ⅲ | a | 78.3 | 40.2 | 137.9 | -189.4 |
| b | 573.0 | 569.2 | 578.1 | -4.4 | |
| c | 848.7 | 797.6 | 917.9 | -68.8 | |
| d | 982.0 | 943.0 | 992.5 | -41.9 | |
| e | 1 057.6 | 1 045.2 | 1 113.2 | -66.9 | |
| Ⅳ | a | 133.4 | 105.0 | 145.1 | -17.1 |
| b | 663.2 | 617.2 | 684.5 | -105.9 | |
| c | 818.3 | 804.1 | 851.9 | -233.6 | |
| d | 1 257.8 | 1 249.7 | 1 267.9 | -15.8 |
表4 四组配方样品所得TG-DSC曲线中主要峰点及峰面积
Table 4 Key peaks and peak areas derived from TG-DSC curves of samples for four batch formulations
| Formulation No. | Peak | Peak temperature/℃ | Onset temperature/℃ | End temperature/℃ | Peak area/(J·g-1) |
|---|---|---|---|---|---|
| Ⅰ | a | 132.3 | 112.5 | 147.0 | -13.8 |
| b | 573.8 | 569.2 | 578.6 | -4.6 | |
| c | 685.9 | 618.1 | 710.7 | -431.0 | |
| d | 815.9 | 806.5 | 828.6 | -58.0 | |
| e | 844.6 | 838.9 | 850.9 | -13.9 | |
| Ⅱ | a | 92.8 | 40.7 | 136.7 | -261.9 |
| b | 268.8 | 254.7 | 283.5 | -7.9 | |
| c | 424.7 | 390.1 | 440.2 | -16.8 | |
| d | 573.5 | 569.2 | 579.3 | -4.2 | |
| e | 914.9 | 898.9 | 936.3 | 15.9 | |
| Ⅲ | a | 78.3 | 40.2 | 137.9 | -189.4 |
| b | 573.0 | 569.2 | 578.1 | -4.4 | |
| c | 848.7 | 797.6 | 917.9 | -68.8 | |
| d | 982.0 | 943.0 | 992.5 | -41.9 | |
| e | 1 057.6 | 1 045.2 | 1 113.2 | -66.9 | |
| Ⅳ | a | 133.4 | 105.0 | 145.1 | -17.1 |
| b | 663.2 | 617.2 | 684.5 | -105.9 | |
| c | 818.3 | 804.1 | 851.9 | -233.6 | |
| d | 1 257.8 | 1 249.7 | 1 267.9 | -15.8 |
| Formulation No. | Endothermic peak area/(J·g-1) | Exothermic peak area/(J·g-1) | ||
|---|---|---|---|---|
| Ⅰ | 521.3 | 0 | 521.3 | 850 |
| Ⅱ | 290.8 | 15.9 | 274.9 | 900 |
| Ⅲ | 371.4 | 0 | 371.4 | 1 000 |
| Ⅳ | 372.4 | 0 | 372.4 | 850 |
表5 四组配方样品的反应热和初始液相形成温度
Table 5 Reaction heat and initial liquid phase formation temperature of samples for four batch formulations
| Formulation No. | Endothermic peak area/(J·g-1) | Exothermic peak area/(J·g-1) | ||
|---|---|---|---|---|
| Ⅰ | 521.3 | 0 | 521.3 | 850 |
| Ⅱ | 290.8 | 15.9 | 274.9 | 900 |
| Ⅲ | 371.4 | 0 | 371.4 | 1 000 |
| Ⅳ | 372.4 | 0 | 372.4 | 850 |
| Formulation No. | ||||
|---|---|---|---|---|
| Ⅰ | 521.3 | 1 106.2 | 633.5 | 2 261.0 |
| Ⅱ | 274.9 | 1 048.5 | 460.7 | 1 784.1 |
| Ⅲ | 371.4 | 1 121.3 | 620.6 | 2 113.3 |
| Ⅳ | 372.4 | 1 019.9 | 509.9 | 1 902.2 |
表6 四组配方进行玻璃生产过程的理论总热耗
Table 6 Theoretical total heat consumption of glass production process for four batch formulations
| Formulation No. | ||||
|---|---|---|---|---|
| Ⅰ | 521.3 | 1 106.2 | 633.5 | 2 261.0 |
| Ⅱ | 274.9 | 1 048.5 | 460.7 | 1 784.1 |
| Ⅲ | 371.4 | 1 121.3 | 620.6 | 2 113.3 |
| Ⅳ | 372.4 | 1 019.9 | 509.9 | 1 902.2 |
| Formulation No. | Component | M/g | MF/% | EF/g | F/% | |
|---|---|---|---|---|---|---|
| Ⅰ | CaCO3 | 13.5 | 99 | 44/100 | 100 | 5.9 |
| Na2CO3 | 24.3 | 99 | 44/106 | 100 | 10.0 | |
| Li2CO3 | 0.4 | 99 | 44/74 | 100 | 0.2 | |
| Total | — | — | — | — | 16.1 | |
| Ⅱ | — | — | — | — | — | 0 |
| Ⅲ | — | — | — | — | — | 0 |
| Ⅳ | CaCO3 | 6.2 | 99 | 44/100 | 100 | 2.7 |
| Na2CO3 | 11.2 | 99 | 44/106 | 100 | 4.6 | |
| Li2CO3 | 0.2 | 99 | 44/74 | 100 | 0.1 | |
| Total | — | — | — | — | 7.4 |
表7 四组配方中由碳酸盐分解产生的碳排放值
Table 7 Carbon emission values produced by carbonate decomposition of four batch formulations
| Formulation No. | Component | M/g | MF/% | EF/g | F/% | |
|---|---|---|---|---|---|---|
| Ⅰ | CaCO3 | 13.5 | 99 | 44/100 | 100 | 5.9 |
| Na2CO3 | 24.3 | 99 | 44/106 | 100 | 10.0 | |
| Li2CO3 | 0.4 | 99 | 44/74 | 100 | 0.2 | |
| Total | — | — | — | — | 16.1 | |
| Ⅱ | — | — | — | — | — | 0 |
| Ⅲ | — | — | — | — | — | 0 |
| Ⅳ | CaCO3 | 6.2 | 99 | 44/100 | 100 | 2.7 |
| Na2CO3 | 11.2 | 99 | 44/106 | 100 | 4.6 | |
| Li2CO3 | 0.2 | 99 | 44/74 | 100 | 0.1 | |
| Total | — | — | — | — | 7.4 |
| Formulation No. | CC/(g·J-1) | OF/% | EF | AD/J | |
|---|---|---|---|---|---|
| Ⅰ | 15.3×10-6 | 99 | 55.5×10-6 | 226 103.9 | 12.5 |
| Ⅱ | 178 406.3 | 9.9 | |||
| Ⅲ | 211 325.9 | 11.7 | |||
| Ⅳ | 190 216.0 | 10.6 |
表8 燃料燃烧所产生的碳排放值
Table 8 Carbon emission values produced by fuel combustion
| Formulation No. | CC/(g·J-1) | OF/% | EF | AD/J | |
|---|---|---|---|---|---|
| Ⅰ | 15.3×10-6 | 99 | 55.5×10-6 | 226 103.9 | 12.5 |
| Ⅱ | 178 406.3 | 9.9 | |||
| Ⅲ | 211 325.9 | 11.7 | |||
| Ⅳ | 190 216.0 | 10.6 |
| Formulation No. | Reduction vs. No. I/% | |||
|---|---|---|---|---|
| Ⅰ | 16.1 | 12.5 | 28.6 | 0 |
| Ⅱ | 0 | 9.9 | 9.9 | 65.4 |
| Ⅲ | 0 | 11.7 | 11.7 | 59.1 |
| Ⅳ | 7.4 | 10.6 | 18.0 | 37.1 |
表9 四组配方在玻璃生产过程中的碳排放总量及差异
Table 9 Total carbon emission amount and differences in glass production process for four batch formulations
| Formulation No. | Reduction vs. No. I/% | |||
|---|---|---|---|---|
| Ⅰ | 16.1 | 12.5 | 28.6 | 0 |
| Ⅱ | 0 | 9.9 | 9.9 | 65.4 |
| Ⅲ | 0 | 11.7 | 11.7 | 59.1 |
| Ⅳ | 7.4 | 10.6 | 18.0 | 37.1 |
| [1] | MA X Q, PENG T D, ZHANG Y R, et al. Accelerating carbon neutrality could help China’s energy system align with below 1.5 ℃[J]. Journal of Environmental Management, 2023, 337: 117753. |
| [2] | REN X H, ZHANG X, YAN C, et al. Climate policy uncertainty and firm-level total factor productivity: evidence from China[J]. Energy Economics, 2022, 113: 106209. |
| [3] | XIAN Y J, HU Z H, WANG K. The least-cost abatement measure of carbon emissions for China’s glass manufacturing industry based on the marginal abatement costs[J]. Energy, 2023, 284: 129159. |
| [4] | MAWLUD S Q, AHMED A A, HAMAD H L, et al. Impact of tempering process on physical, optical and hardness properties of soda-lime glass[J]. Journal of Materials Engineering and Performance, 2025: 1-9. |
| [5] | FURSZYFER DEL RIO D D, SOVACOOL B K, FOLEY A M, et al. Decarbonizing the glass industry: a critical and systematic review of developments, sociotechnical systems and policy options[J]. Renewable and Sustainable Energy Reviews, 2022, 155: 111885. |
| [6] | CAUDLE B, TANIGUCHI S, NGUYEN T T H, et al. Integrating carbon capture and utilization into the glass industry: economic analysis of emissions reduction through CO2 mineralization[J]. Journal of Cleaner Production, 2023, 416: 137846. |
| [7] | MEECHOOWAS E, KETBOONRUANG P, TAPASA K, et al. Improve melting glass efficiency by batch-to melt conversion[J]. Procedia Engineering, 2012, 32: 956-961. |
| [8] | LI H, DEMIROK G, IBARRA-MUNOZ P, et al. Effects of alternative natural silicates on the kinetics of batch-to-melt conversion for E-Glass fiber[J]. International Journal of Applied Glass Science, 2025, 16: e16690. |
| [9] | MEECHOOWAS E, TAPASA K, JITWATCHARAKOMOL T. Alternative soda-lime glass batch to reduce energy consumption[J]. Key Engineering Materials, 2013, 545: 24-30. |
| [10] | ALFONSO P, TOMASA O, GARCIA-VALLES M, et al. Potential of tungsten tailings as glass raw materials[J]. Materials Letters, 2018, 228: 456-458. |
| [11] | ALFONSO P, TOMASA O, GARCIA-VALLES M, et al. Glass-ceramic crystallization from tailings of the Morille tungsten deposit, Spain[J]. Materials Letters, 2022, 312: 131694. |
| [12] | KUŚNIERZ A A, SZUMERA M, KOSMAL M, et al. Influence of the increased content of Calumite blast-furnace slag on the melting of sodium-calcium-silicate glass[J]. Journal of Thermal Analysis and Calorimetry, 2019, 138(6): 4571-4583. |
| [13] | PAULıUKEVıCH Y, PAPKO L, TRUSOVA E, et al. Effect of aluminum-containing raw materials on the melting of borosilicate glass for fiber[J]. Ceramics International, 2021, 47(22): 31092-31098. |
| [14] | BRISTOGIANNI T, OIKONOMOPOULOU F. Glass up-casting: a review on the current challenges in glass recycling and a novel approach for recycling “as-is” glass waste into volumetric glass components[J]. Glass Structures & Engineering, 2023, 8(2): 255-302. |
| [15] | KOVAČEC M, PILIPOVIĆ A, ŠTEFANIĆ N. Impact of glass cullet on the consumption of energy and environment in the production of glass packaging material[J]. Recent Researches in Chemistry, Biology, Environment and Culture, 2011, 187-192. |
| [16] | ZHANG L X, LIANG L S, LI Y, et al. Preparation of lightweight foam glass-ceramics from copper slag tailings: secondary aluminum slag as pore-forming agent[J]. Ceramics International, 2024, 50(21): 43699-43709. |
| [17] | BESSMERTNYI V S, BONDARENKO M A, ZDORENKO N M, et al. Composite glass-crystalline material based on cullet and colemanite[J]. Inorganic Materials: Applied Research, 2023, 14(1): 64-69. |
| [18] | BENSEND A, ZACCARIA M. Reducing deflection of thin glass by prestress[J]. Challenging Glass Conference Proceedings, 2024, 9: 1-15. |
| [19] | ZHOU Z W, REN W L, LIN Y X, et al. Waste-derived glass-ceramic LTCC materials prepared from waste soda-lime-silicate glass and waste asbestos wool[J]. Journal of Non-Crystalline Solids, 2023, 621: 122602. |
| [20] | DENG W, BACKHOUSE D J, KAZI F K, et al. Alternative raw material research for decarbonization of UK glass manufacture[J]. International Journal of Applied Glass Science, 2023, 14(3): 341-365. |
| [21] | DENG W, SPATHI C, COULBECK T, et al. Exploratory research in alternative raw material sources and reformulation for industrial soda-lime-silica glass batches[J]. International Journal of Applied Glass Science, 2020, 11(2): 340-356. |
| [22] | WANG J Y, FU J Y, ZHAO Z T, et al. Benefit analysis of multi-approach biomass energy utilization toward carbon neutrality[J]. The Innovation, 2023, 4(3): 100423. |
| [23] | LEICHER J, GIESE A, WIELAND C. Electrification or hydrogen? the challenge of decarbonizing industrial (high-temperature) process heat[J]. J-Multidisciplinary Scientific Journal, 2024, 7(4): 439-456. |
| [24] | FRAGAPANE G, WAN P K, ORTIZ M M, et al. Impact of hydrogen integration and implementation on costs in glass production[J]. Procedia CIRP, 2024, 130: 1776-1783. |
| [25] | ADI SASONGKO N, GUNADI PUTRA N, DONNA WARDANI M L. Review of types of biomass as a fuel-combustion feedstock and their characteristics[J]. Advances in Food Science, Sustainable Agriculture and Agroindustrial Engineering, 2023, 6(2): 170-184. |
| [26] | ZHAO X G, LIU P K. Substitution among energy sources: an empirical analysis on biomass energy for fossil fuel of China[J]. Renewable and Sustainable Energy Reviews, 2013, 18: 194-202. |
| [27] | VAN DEN OEVER A E M, COSTA D, CARDELLINI G, et al. Systematic review on the energy conversion efficiency of biomass-based Fischer-Tropsch plants[J]. Fuel, 2022, 324: 124478. |
| [28] | ALSUNOUSI M, KAYABASI E. The role of hydrogen in synthetic fuel production strategies[J]. International Journal of Hydrogen Energy, 2024, 54: 1169-1178. |
| [29] | YAO Y, HE J Y, CHEN Q, et al. Analysis of energy, exergy and CO2 emissions in a fiberglass furnace with oxy-fuel combustion[J]. Fuel, 2023, 348: 128484. |
| [30] | QI Y F, WANG C Y, ZHANG M H, et al. Comparative analysis of combustion characteristics and economy between air assisted combustion and oxy-fuel combustion in glass furnaces[J]. Thermal Science and Engineering Progress, 2024, 53: 102699. |
| [31] | HUANG X Y, YANG Z Y, NING K X, et al. Numerical investigation of combustion characteristics under oxygen-enriched combustion combined with flue gas recirculation in a cement rotary kiln[J]. Applied Thermal Engineering, 2023, 233: 121106. |
| [32] | WANG H Y, YANG X, LI Z Y, et al. Numerical investigation on the effect of air humidification and oxygen enrichment on combustion and emission characteristics of gas boiler[J]. Processes, 2024, 12(10): 2282. |
| [33] | JOST D, KANZUROVA S, NILGES B, et al. Life cycle assessment of measures towards a low-carbon flat glass production[J]. Journal of Cleaner Production, 2025, 501: 145294. |
| [34] | GALAN I, GLASSER F P, ANDRADE C. Calcium carbonate decomposition[J]. Journal of Thermal Analysis and Calorimetry, 2013, 111(2): 1197-1202. |
| [35] | JONES A R, WINTER R, NEVILLE GREAVES G, et al. 23Na, 29Si, and 13C MAS NMR investigation of glass-forming reactions between Na2CO3 and SiO2 [J]. The Journal of Physical Chemistry B, 2005, 109(49): 23154-23161. |
| [36] | KIM J W, LEE Y D, LEE H G. Decomposition of Na2CO3 by interaction with SiO2 in mold flux of steel continuous casting[J]. ISIJ International, 2001, 41(2): 116-123. |
| [1] | 曹志强, 李苑, 金良茂, 于浩, 曹欣, 刘涌, 韩高荣. 融合CBAM机制的ResNet34模型用于电子基板玻璃热工缺陷分类研究[J]. 硅酸盐通报, 2026, 45(3): 1074-1082. |
| [2] | 董发鑫, 徐子凡, 汪峻峰, 鲁刘磊, 叶伟开, 尚春静. 高强硫铝酸盐水泥基材料固化垃圾焚烧飞灰的试验研究[J]. 硅酸盐通报, 2025, 44(9): 3280-3287. |
| [3] | 于新, 王龙, 何平平, 刘雨松. 以黄金尾矿砂为细骨料的工程水泥基复合材料性能研究[J]. 硅酸盐通报, 2025, 44(7): 2566-2577. |
| [4] | 夏陈晨, 徐浩, 周泽, 翟文强, 何智海. 再生微粉自流平砂浆性能及碳排放分析[J]. 硅酸盐通报, 2025, 44(4): 1477-1485. |
| [5] | 王凡, 龙广成, 白敏, 石莹莹. 电解锰渣基绿色混凝土性能及环境效应分析[J]. 硅酸盐通报, 2025, 44(4): 1386-1397. |
| [6] | 王一晓, 许耀群, 张昂, 林新昊, 杨嫚嫚. 矿化养护碱激发固废胶凝材料性能与环境影响的综合评价[J]. 硅酸盐通报, 2024, 43(3): 977-986. |
| [7] | 丁超, 贾子杰, 王振华, 丁玉贤. 基于生命周期评价的UHPC碳排放控制潜力评估[J]. 硅酸盐通报, 2023, 42(4): 1242-1251. |
| [8] | 周明凯, 柳剑锋, 葛雪祥, 栗振宇. 粉煤灰发泡陶瓷的制备及性能研究[J]. 硅酸盐通报, 2021, 40(2): 605-609. |
| [9] | 韩保东;刘阳;魏士华;郑克仁. 基于反向填充制备低碳水泥基材料[J]. 硅酸盐通报, 2020, 39(2): 389-395. |
| [10] | 田璐璐;王姗姗;王克;岳辉;王逸欣;刘磊;张瑞芹. 河南省水泥行业节能潜力及协同减排效果分析[J]. 硅酸盐通报, 2016, 35(12): 3915-3924. |
| [11] | 李琦;陈延信;赵博;姚艳飞. CaCO3渣悬浮态分解生产线简介及运行分析[J]. 硅酸盐通报, 2014, 33(8): 2105-2108. |
| [12] | 李红建;王国鸿;周刘成;李昌勇. 四级、五级和六级预热预分解窑系统节能效果的探讨[J]. 硅酸盐通报, 2013, 32(4): 566-571. |
| 阅读次数 | ||||||
|
全文 |
|
|||||
|
摘要 |
|
|||||