耐火材料
耐火材料
내화재료
REFRACTORIES
2015年
3期
161-164
,共4页
陈树江%刘耀闻%李国华%张国栋%郝明选%袁林
陳樹江%劉耀聞%李國華%張國棟%郝明選%袁林
진수강%류요문%리국화%장국동%학명선%원림
方镁石-复合尖晶石砖%水泥窑%烧成带%水泥熟料%可燃性废弃物%侵蚀机制
方鎂石-複閤尖晶石磚%水泥窯%燒成帶%水泥熟料%可燃性廢棄物%侵蝕機製
방미석-복합첨정석전%수니요%소성대%수니숙료%가연성폐기물%침식궤제
periclase-compound spine brick%cement rotary kiln%burning zone%cement clinker%combustible waste%corrosion mechanism
为了解采用可燃性废弃物作为替代燃料煅烧水泥熟料时产生的气氛对水泥窑烧成带用方镁石-复合尖晶石砖的侵蚀情况,首先进行了化学试剂 V2 O5分别与高纯镁砂和镁铝尖晶石砂在1500℃下的反应试验;然后以高纯镁砂、高铁镁砂、铁铝尖晶石砂为原料,于1600℃烧成制备了方镁石-复合尖晶石坩埚试样,按水泥熟料、橡胶轮胎、石油焦的质量分数分别为50%、25%、25%配成侵蚀介质,采用静态坩埚法进行了替代燃料对方镁石-复合尖晶石材料的侵蚀试验(1450℃保温3 h)。利用 XRD 检测了试样的物相组成,采用 SEM观察和分析了气氛侵蚀后试样的显微形貌。结果表明:1)V2 O5与 MA 中的 MgO 反应产生刚玉相和钒酸镁,破坏了尖晶石结构,并伴随较大的体积膨胀而破坏了砖的结构。因此,在水泥窑使用替代燃料的情况下,方镁石-复合尖晶石砖中不适合加入镁铝尖晶石。2)替代燃料燃烧产生的 SO3、V2 O5等酸性气体沿着气孔和晶界向砖内扩散,在气孔和晶界处聚集,与方镁石-复合尖晶石材料中的 CaO、MgO 反应生成 Ca3(VO4)2、Mg3(VO4)2、CaSO4、MgSO4,产生体积效应,不利于材料的稳定;另外还与水泥熟料中的 C2 S 反应生成 CaSO4和低熔点相,不利于窑皮的稳定。
為瞭解採用可燃性廢棄物作為替代燃料煅燒水泥熟料時產生的氣氛對水泥窯燒成帶用方鎂石-複閤尖晶石磚的侵蝕情況,首先進行瞭化學試劑 V2 O5分彆與高純鎂砂和鎂鋁尖晶石砂在1500℃下的反應試驗;然後以高純鎂砂、高鐵鎂砂、鐵鋁尖晶石砂為原料,于1600℃燒成製備瞭方鎂石-複閤尖晶石坩堝試樣,按水泥熟料、橡膠輪胎、石油焦的質量分數分彆為50%、25%、25%配成侵蝕介質,採用靜態坩堝法進行瞭替代燃料對方鎂石-複閤尖晶石材料的侵蝕試驗(1450℃保溫3 h)。利用 XRD 檢測瞭試樣的物相組成,採用 SEM觀察和分析瞭氣氛侵蝕後試樣的顯微形貌。結果錶明:1)V2 O5與 MA 中的 MgO 反應產生剛玉相和釩痠鎂,破壞瞭尖晶石結構,併伴隨較大的體積膨脹而破壞瞭磚的結構。因此,在水泥窯使用替代燃料的情況下,方鎂石-複閤尖晶石磚中不適閤加入鎂鋁尖晶石。2)替代燃料燃燒產生的 SO3、V2 O5等痠性氣體沿著氣孔和晶界嚮磚內擴散,在氣孔和晶界處聚集,與方鎂石-複閤尖晶石材料中的 CaO、MgO 反應生成 Ca3(VO4)2、Mg3(VO4)2、CaSO4、MgSO4,產生體積效應,不利于材料的穩定;另外還與水泥熟料中的 C2 S 反應生成 CaSO4和低鎔點相,不利于窯皮的穩定。
위료해채용가연성폐기물작위체대연료단소수니숙료시산생적기분대수니요소성대용방미석-복합첨정석전적침식정황,수선진행료화학시제 V2 O5분별여고순미사화미려첨정석사재1500℃하적반응시험;연후이고순미사、고철미사、철려첨정석사위원료,우1600℃소성제비료방미석-복합첨정석감과시양,안수니숙료、상효륜태、석유초적질량분수분별위50%、25%、25%배성침식개질,채용정태감과법진행료체대연료대방미석-복합첨정석재료적침식시험(1450℃보온3 h)。이용 XRD 검측료시양적물상조성,채용 SEM관찰화분석료기분침식후시양적현미형모。결과표명:1)V2 O5여 MA 중적 MgO 반응산생강옥상화범산미,파배료첨정석결구,병반수교대적체적팽창이파배료전적결구。인차,재수니요사용체대연료적정황하,방미석-복합첨정석전중불괄합가입미려첨정석。2)체대연료연소산생적 SO3、V2 O5등산성기체연착기공화정계향전내확산,재기공화정계처취집,여방미석-복합첨정석재료중적 CaO、MgO 반응생성 Ca3(VO4)2、Mg3(VO4)2、CaSO4、MgSO4,산생체적효응,불리우재료적은정;령외환여수니숙료중적 C2 S 반응생성 CaSO4화저용점상,불리우요피적은정。
This paper aims at researching the produced atmosphere corrosion during the calcination of ce-ment clinker using combustible wastes as substitute fuels to periclase-compound spinel bricks for burning zone of cement kilns.Firstly,chemical reactions between V2 O5 and high purity magnesia or magnesium alu-minate spinel at 1 500 ℃ were researched.Secondly,periclase-compound spinel crucible specimens were prepared at 1 600 ℃ using high purity magnesia,ferruginous magnesia,and hercynite as raw materials;the corrosion medium was prepared using 50% cement clinker,25% rubber tyre and 25% petroleum coke;the static crucible corrosion tests were carried out at 1 450 ℃ for 3 h.The microstructure and phase composition of the corroded specimens were analyzed by SEMand XRD,respectively.It is found that (1)V2 O5 reacts with MgO from spinel forming corundum and magnesium vanadate accompanied by a large volume expansion, deteriorating the spinel structure,thus damaging the brick structure,so when the substitute fuels are used for cement kilns,magnesium aluminate spinel is not a suitable raw material for periclase-compound spinel bricks;(2)the produced acid gases such as SO3 and V2 O5 during the combustion of alternative fuels pene-trate into the bricks along pores and crystal interfaces,gather in pores and crystal interfaces,react with CaO and MgO from periclase-compound spinel bricks forming Ca3 (VO4 )2 ,Mg3 (VO4 )2 ,CaSO4 and MgSO4 ac-companied by volume effect,which is disadvantage to the brick stability;additionally,the acid gases react with C2 S forming low melting phases and CaSO4 ,which goes against the stability of kiln coating.