Bioreactor designs for solid state fermentation
Development of a Microreactor for Solid Phase Synthesis
1.2
Solid Phase Organic Chemistry
One of today's most effective and reliable methods for the preparation of large libraries is based on the use of solid phase organic synthesis due to the ease of its automation and the good purities of the final products. This technology - the build up of a molecule on a template which is covalently bonded via a linker to a polymer support, followed by cleavage of the bond to the linker - has been developed to a very reliable tool in parallel synthesis [5]. The main advantages are: • The ease of driving a reaction to completion by employing excess reagent which can be washed off after the reaction. • The avoidance of difficult purification steps such as chromatography, distillation or crystallization. SPOS needs only few repetitive unit operations which have to be realized under inert conditions: • Addition of liquid reagents / solvents • Agitation • Filtration • Heating / cooling
紫外光解法在制备低介电常数氧化硅分子筛薄膜中的应用
[Article]物理化学学报(Wuli Huaxue Xuebao )Acta Phys.鄄Chim.Sin .,2007,23(8):1219-1223August Received:January 9,2007;Revised:April 6,2007;Published on Web:June 13,2007.∗Corresponding author.Email:qhli@;Tel:+8621⁃50217337.国家自然科学基金青年基金(50503011),上海“浦江人才”计划(05PG14051),上海市教委重点项目(06zz95)及上海市重点学科项目(P1701)资助ⒸEditorial office of Acta Physico ⁃Chimica Sinica紫外光解法在制备低介电常数氧化硅分子筛薄膜中的应用袁昊1李庆华1,∗沙菲2解丽丽1田震1王利军1(1上海第二工业大学环境工程系,上海201209;2上海纳米材料检测中心,上海200237)摘要:以正硅酸乙酯为硅源,四丙基氢氧化铵(TPAOH)为模板剂和碱源,采取水热晶化技术,通过原位法在硅晶片表面制备出纯二氧化硅透明分子筛薄膜;采用紫外光解法代替传统高温焙烧法脱除分子筛薄膜孔道内的模板剂,制备出具有低介电常数的氧化硅分子筛薄膜.使用FTIR 、XRD 和SEM 对样品进行了结构表征,并采用阻抗分析仪测量了薄膜的介电常数,纳米硬度计测量薄膜的杨氏模量和硬度.与传统的高温焙烧方法相比,紫外光解法处理条件温和,同时省时、省能、操作简易.关键词:紫外光解法;高温焙烧法;氧化硅分子筛薄膜;低介电常数中图分类号:O649Application of Ultraviolet Treatment in the Synthesis of Pure 鄄silicaZeolite Thin Films with Low Dielectric ConstantYUAN Hao 1LI Qing ⁃Hua 1,∗SHA Fei 2XIE Li ⁃Li 1TIAN Zhen 1WANG Li ⁃Jun 1(1Department of Environmental Engineering,Shanghai Second Polytechnic University,Shanghai 201209,P.R.China ;2Shanghai Testing Center of Nanometer Materials,Shanghai 200237,P.R.China )Abstract :Transparent pure ⁃silica zeolite (PSZ)films were synthesized on silicon wafers through hydrothermal reaction ,in which tetraethyl orthosilicate (TEOS)was used as silica source ,tetrapropyl ammonium hydroxide (TPAOH)as template and alkaline source.An ultraviolet treatment was subsequently applied to remove the organic templates within the pores/channels of zeolite films.The thin films were characterized by using FTIR,XRD,and SEM techniques before and after the ultraviolet treatment.FTIR results showed that the organic templates were effectively removed via ultraviolet treatment,which was the same as the results from the calcinations treatment.In comparison with the calcined films,XRD and SEM results indicated that the crystallinity and the surface as well as the thickness of the films had no significant changes after ultraviolet treatment.Dielectric constant (ε)values of the thin films were measured by means of impedance analyzer.Elastic modulus and hardness of the thin films were measured by the nano ⁃indentation technique.All results showed that the films after ultraviolet treatment had a lower εvalue and higher mechanical strength.Therefore,it could be concluded that ultraviolet treatment was a faster,more energy ⁃conservative method to remove template from zeolite films,in comparison with conventional calcination.Key Words :Ultraviolet treatment;Calcination;Silica zeolite thin film;Low dielectric constant随着超大规模集成电路(ULSI)技术的发展,电子器件特征尺寸不断缩小,而电路的互连延迟逐渐增大[1,2],成为制约集成电路速度进一步提高的瓶颈.采用低介电常数(low ε)介质薄膜作金属线间和层间介质以代替传统SiO 2介质(ε≈4)是降低互连延迟、串扰和能耗的有效方法[2,3].通常采取以下两类方法降低材料的介电常数:第一类是利用有机化合物本身的低介电常数特性,但由于其机械性能差又不耐高温等缺陷限制了它们的应用;第二类是降低材料的有效介电常数,即在材1219Acta Phys.鄄Chim.Sin.,2007Vol.23料中增加孔隙,制备成多孔薄膜的方法.由于孔隙的增多致使平均介电常数降低.目前有可能在集成电路中应用的低介电常数介质主要有多孔氧化硅、含氟氧化硅、含氟碳膜、聚酰亚胺等[4-7].其中多孔SiO2不仅有较低的介电常数,且能与已有的单晶SiO2工艺很好地兼容,在热稳定性、对无机物的粘附性等方面明显优于有机介质,是传统SiO2理想的替代物.纳米多孔SiO2材料的制备目前多采用溶胶⁃凝胶(sol⁃gel)工艺[7,8],采用这种方法可获得较大孔隙度,但孔的结构不易控制,孔径尺寸随机分布,不适于用在集成电路中作为互连介质.另一类是与溶胶⁃凝胶技术相结合的模板法,以表面活性剂为模板,结合溶胶⁃凝胶或旋涂技术,可以得到孔径分布均匀的纳米介孔SiO2材料[9,10].与单纯的溶胶⁃凝胶方法相比,这种模板合成法可合理地控制孔隙度、孔尺寸以及膜的结构和厚度,但该类介孔薄膜材料易吸附空气中的水,从而导致薄膜的介电常数增大;同时,其薄膜材料较大的孔道和疏松的无机孔壁结构导致膜的机械性能下降,限制了介孔SiO2材料的进一步应用.近年来,一种新型基于微孔二氧化硅晶体———纯二氧化硅分子筛薄膜材料开始引起人们的关注.同具有低介电常数的有机硅酸盐、氟化硅玻璃或介孔二氧化硅薄膜相比,氧化硅分子筛薄膜具有均一的孔道结构,高热稳定性,高机械强度和高疏水性等特性[11,12],并且具有较低的理论介电常数[13].美国加州大学Yan课题组最先合成的MFI分子筛薄膜的ε值可达到2.7[14].通过选用较低骨架密度的MFI型分子筛或添加造孔剂等方法,将ε值进一步降低到2.2以下[15,16].最引人注目的是这种新型材料的机械强度(杨氏模量E)远大于其它材料[17],因此氧化硅分子筛薄膜有望代替传统二氧化硅薄膜而应用在未来超低ε材料领域.然而,尽管纯硅沸石分子筛(PSZ)薄膜材料显示出比纳米多孔SiO2材料更优异的机械强度和疏水性能,但在制备后期需要采用高温焙烧(>500℃)的方法脱除阻塞孔道的模板剂,并且加热处理过程比较缓慢.我们知道,低介电常数薄膜在实际制备中使用的温度一般不高于400℃.因此,如何解决在低温下快速有效地脱除有机模板剂成为氧化硅分子筛薄膜可以在低ε材料领域得到实际应用的关键问题.目前报道的脱除有机模板剂常用的方法除传统的高温焙烧外,还有酸萃取法和微波消解法等.但温和的酸萃取剂不能彻底脱除模板剂,而微波消解法在结合以廉价氧化性无机酸等为溶剂,利用体系中自身的压力脱除模板剂的同时对薄膜的骨架会有一定的副作用.Li等[18,19]将紫外光解技术应用在微孔分子筛领域,制备出一系列性能良好的分子筛纳米颗粒和薄膜.区别于传统的高温焙烧法,紫外光解技术是在近室温条件下将有机模板剂进行光化学分解,不仅避免高温对低介电常数材料制备影响的限制,同时也避免高温导致的薄膜材料和薄膜基底热膨胀系数不同产生的薄膜开裂.本研究是在原有工作基础上,继续探索紫外光解技术在制备低介电常数氧化硅分子筛薄膜方面的优越性.通过水热晶化方法,以四丙基氢氧化铵(TPAOH)为模板剂,在硅晶片上原位制备高质量的氧化硅分子筛薄膜.比较了传统高温焙烧法和紫外光解法对薄膜结构、组成和介电常数等的影响.1实验过程1.1原位晶化制备氧化硅分子筛薄膜将2cm×2cm双面抛光的硅晶片严格按标准的硅芯片清洗步骤清洗后,固定在自制的特富龙支架上,置于TPAOH/TEOS/H2O/EtOH的摩尔比为0.12/1/85/4的澄清溶液中,于100℃油浴中静置,2天后取出硅晶片,用0.1mol·L-1的氨水溶液洗涤后,室温下真空干燥.形成薄膜后,将其中一个薄膜基片放置在184-257nm、10-20mW·cm-2下的中压汞灯下照射3-8 h(在184-257nm波长范围内的紫外光),基片中心离紫外灯下端距离为2cm,控制实验温度<50℃.作为参比,采用传统的高温焙烧脱除模板剂的处理方法,将相同样品在氮气保护下以1℃·min-1的线性升温速率升到550℃,在550℃下焙烧6h,再以1℃·min-1降温速率降到室温,得到参比样品.整个高温焙烧的处理时间长达48h.1.2性能表征采用德国布鲁克AXS公司的D8ADVANCE X⁃ray Diffractometer确定微孔薄膜的晶态结构,使用Cu Kα为射线源,管电压40kV,管电流40mA,扫描区间5°-40°;采用德国布鲁克V70傅立叶变换红外分光光谱仪测定薄膜的红外光谱;用日本日立S⁃4800型冷场扫描电子显微镜观察薄膜的表面形貌和薄膜的厚度;介电常数的测量采用平行电容法,电容由HP4284阻抗分析仪测定;杨氏模量和硬度采用美国MTS公司的纳米压痕仪Nano⁃indenter1220No.8袁昊等:紫外光解法在制备低介电常数氧化硅分子筛薄膜中的应用DCM组件测定.2结果与讨论2.1FTIR图谱分析图1为原位晶化得到的氧化硅分子筛薄膜及其紫外光照处理/高温焙烧后产物的红外光谱图.对处理前的薄膜,图1的插图可直接表明有机分子的存在.模板剂中甲基(CH3)和亚甲基(CH2)的C—H伸缩振动峰在2700-3100cm-1区域之间,甲基(CH3)的C—H弯曲振动在1300-1600cm-1区域之间.图1高波数段(3100-2700cm-1)显示在2883、2943、2981 cm-1处有三个吸收峰,这些分别归属于亚甲基(CH2)和甲基(CH3)的C—H伸缩振动,而在低波数段(1800-500cm-1)的1460、1474cm-1处的两个吸收峰则归属于模板剂亚甲基(CH2)和甲基(CH3)的C—H 弯曲振动[20].经过高温焙烧和紫外光照处理后FTIR图谱发生了一些明显的变化.表征有机模板剂的甲基(CH3)和亚甲基(CH2)的C—H伸缩振动和弯曲振动的特征谱峰全部消失,表明两种处理方式都能有效地脱去孔道内的模板剂(低于仪器的检测下限,残留有机物低于1%的原始含量).目前对UV/ozone空气环境下降解有机物的机理学术界还存在争论,但普遍认为UV光照过程可能包括下面的反应:低于245.4nm(最佳λ=184nm)的紫外光照促进了氧气(空气中的)分裂成臭氧和氧原子;且253.7nm波长的光线可激活和/或分裂有机基体,从而产生有活性的核素(如离子、自由基和受激分子);有活性的有机核素随时受到氧原子和臭氧的协同攻击容易形成简单的易挥发的(或可除去的)产物,如一些可从样品内部逸出的CO2、H2O和N2.同时,UV光源发出的光子表现的热效应[21],促使薄膜内部的有机成分分解挥发,且在较短的时间内使得薄膜的性能达到甚至超过传统的热处理效果.需要指出的是,脱除模板剂及其分解产物所需的紫外照射时间与使用的汞灯的功率、灯管清洁程度、薄膜离灯的距离以及薄膜自身的厚度等因素有关.红外测量结果表明,4h的照射时间足够完全除去分子筛薄膜孔道内的有机物,并且能保持样品表面的温度低于50℃,而高温焙烧法不仅需要高达550℃的高温,而且加热时间需要至少48h.所以,紫外光照技术应用在薄膜领域具有低温、快速、简易的特点,在保障低温脱除模板剂前提下,又大大缩短了模板剂脱除所需的时间.2.2XRD图谱分析图2是原位晶化后的分子筛薄膜和经紫外光照或高温焙烧处理后的XRD图谱.薄膜未经处理前的XRD图谱是MFI分子筛薄膜典型的特征衍射峰[22],表明薄膜材料具有均一有序的孔洞结构.样品经过紫外光照或高温焙烧处理后,峰位保持不变,峰的相对强度发生了明显的变化.前两个峰7.96°和8.88°的峰强度变强,11.92°和12.50°两个峰强度有所下降,这主要是由于在模板剂脱除过程中无机组分进入到骨架结构的空穴中[23].我们知道,分子筛薄膜在高温焙烧脱除有机模板剂过程中常会引起薄膜结晶度的下降,这将导致孔隙率降低,介电常数ε值增大.为避免破坏薄膜结构,通常采用氧气/氮气气氛下非常缓慢的程序控制升温过程.整个实验过程耗时、耗能,同时高温可能引起薄膜因与基底热膨胀系数不同而产生裂纹,大图1MFI薄膜原样、UV光照或焙烧处理后的FTIR图谱Fig.1FTIR absorption spectra of silica MFI films ofas⁃synthesized and treated by UV and calcinationMFI:a kind of silicazeolites图2MFI薄膜原样、UV光照/高温焙烧处理后的XRD图Fig.2XRD patterns of silica MFI films of as⁃synthesized and treated by UV and calcination1221Acta Phys.⁃Chim.Sin.,2007Vol.23大影响膜的性能.而紫外光照处理后的XRD 谱图证实紫外光照技术在高效除去模板剂的同时,在保持薄膜结晶度和完整性方面具有比传统高温焙烧法更优异的性能.2.3SEM 形貌厚度分析图3是原位晶化后的微孔分子筛薄膜和经紫外光照或高温焙烧处理后的扫描电镜照片.照片显示,无论是紫外光照处理还是高温焙烧,薄膜表面同未处理前的表面形貌没有明显差异.薄膜表面致密、连续、平整.从SEM 的截面图象中观察到三种薄膜的厚度非常接近,平均为500nm.说明紫外光照处理同高温焙烧处理一样,对薄膜厚度没有影响.2.4薄膜介电常数分析FTIR 和XRD 谱图分析表明紫外光解法比传统高温焙烧法在脱除薄膜孔道内的有机物过程中不仅保证整个过程是低温、快速进行,同时在保持薄膜结晶度完整方面紫外光解法具有更大的优势.我们进一步用平行电容法测量了两种薄膜的介电常数值,研究不同处理方法对介电常数值的影响.为了测量薄膜的介电常数,在制备好的薄膜表面通过孔状隔板真空蒸发上直径为1.5mm 、厚度为1μm 的6个圆形铝点作为上层电极,在硅片的另一面先用缓冲的HF 溶液清洗后真空蒸发沉积一层铝膜,这样它连同中间层的氧化硅介质及上层的铝点构成平板电容器.微孔薄膜的相对介电常数通过公式ε=Cd /(A ε0)算出,其中A 是圆形铝电极的面积,ε0是真空介电常数,d 是薄膜厚度,电容C 由HP4284阻抗分析仪测定.为了避免水吸附的影响,待测薄膜先在120℃下干燥12h,然后保存在干燥器中.电容测量过程在N 2保护下进行.处理前薄膜的介电常数值为ε=3.6,经紫外光照处理后ε=2.4,而经高温焙烧处理后的ε=2.6.这是由于原位晶化制备的分子筛薄膜因孔道中的模板剂占据了一定的空间,导致孔隙率降低,所以介电常数ε值较高为3.6,但经紫外光照处理和高温焙烧脱除模板剂后,ε值因孔隙的增大而分别降低到2.4和2.6,大大低于目前普遍使用的SiO 2介电材料(ε≈4).紫外光照处理比高温焙烧后的ε值低的实验结果也进一步证实了XRD 图谱分析的预测,即由紫外光照处理的样品比高温处理的样品结构更加有序、结晶度更高、缺陷更少.由此,分子筛薄膜的孔隙率增大,ε值减小.2.5薄膜杨氏模量分析经高温焙烧处理后薄膜的杨氏模量和硬度分别为43.2GPa 和2.67GPa,经紫外光照处理后薄膜的杨氏模量和硬度分别为44.0GPa 和2.73GPa.经过紫外光照和高温焙烧处理脱除模板剂后的杨氏模量分别为44.0GPa 和43.2GPa,远远高于微电子工业所要求的低ε材料的杨氏模量必须大约6GPa 的要求.同时由于紫外光解法相对于高温焙烧法具有更好的结构有序度、空间缺陷少等优点,使其具备了更好的机械性能.3结论FTIR 、XRD 、SEM 表征结果和介电常数、机械性能分析表明,紫外光解法同传统的高温焙烧处理法相比,不仅在低温(<50℃)下有效地脱除分子筛薄膜模板剂,而且大大缩短脱除模板剂所需的时间(从48h 降低到4h).需要指出的是,紫外光解法比传统高温焙烧方法在保持薄膜结晶度、有序性方面具有更大的优势,同时可以避免因膜与基底间的热膨胀系数不同而导致在膜界面产生裂缝,因此,在制备高质量低介电常数的薄膜材料方面具有独特的优越性.References1Chen,S.J.;Evans,D.F.;Ninham,B.M.J.Phys.Chem.,1984,88:16312Banerjee,K.;Amerasekera,A.;Dixit,G.;Hu,C.Technical Digest of IEEE International Electron Device Meeting.San Francisco,1996:65-683Fan,H.Y.;Bentley,H.R.;Kathan,K.R.;Clem,Y.;Lu,Y.;Brink,C.J.J.Non ⁃Cryst.Solids,2001,285:79图3薄膜的SEM 照片Fig.3SEM micrographs of films(a)as ⁃synthesized film,(b)UV treated film,(c)calcined film(a)(b)(c)1222No.8袁昊等:紫外光解法在制备低介电常数氧化硅分子筛薄膜中的应用4Bhan,M.K.;Huang,J.;Cheung,D.Thin Solid Films,1997,308/ 309:5075Kazuhiko,E.;Toru,T.J.Vac.Sci.Technol.,1997,15(6):3134 6Lu,T.M.;Moore,J.A.MRS Bulletin,1997,22(10):287Homma,T.Material Science and Engineering,1998,23(6):243 8Wu,G.M.;Shen,J.;Wang,J.;Zhou,B.;Ni,X.Y.Atomic Energy Science and Technology,2002,36(4/5):374[吴广明,沈军,王珏,周斌,倪星元.原子能科学技术,2002,36(4/5):374] 9Stupp,S.I.;Lebonheur,V.;Walker,K.;Li,L.S.;Huggins,K.E.Science,1997,276:38410Wang,J.;Zhang,C.R.;Feng,J.Acta Phys.⁃Chim.Sin.,2004,20(12):1399[王娟,张长瑞,冯坚.物理化学学报,2004,20(12):1399]11Wang,Z.B.;Mitra,A.P.;Wang,H.T.;Yan,Y.Adv.Mater., 2001,13:74612Persson,A.E.;Schoeman,B.J.;Sterte,J.Zeolites,1995,15:611 13van Santen,P.A.;Kramer,G.J.Chem.Rev.,1995,95:63714Wang,Z.;Wang,H.;Mitra,A.;Huang,L.;Yan,Y.Adv.Mater.,2001,13:74615Mitra,A.;Cao,T.;Wang,H.;Wang,Z.;Huang,L.Ind.Eng.Chem.Res.,2004,43:294616Li,S.;Li,Z.;Yan,Y.Adv.Mater.,2003,15:152817Li,Z.;Johnson,M.C.;Sun,M.;Ryan,E.;Earl,D.J.Angew.Chem.Int.Ed.,2006,45:632918Parikh,A.;Navrotsky,A.;Li,Q.;Yee,C.K.;Amwg,M.L.Microporous Mesoporous Mat.,2004,76:1719Li,Q.;Amweg,M.;Yee,C.Microporous Mesoporous Mat.,2005, 87:4520Bellamy,L.J.The infrared sepctra of complex molecules.London: Chapman and Hall,1975:374-38321Taylor,D.J.;Fabes,B.D.J.Non⁃Cryst.Solids,1992,147-148: 45722Wu,E.L.;Lawton,S.L.;Oison,D.H.;Rohrman,A.C.J.Phys.Chem.,1979,83(21):277723Flanigen,E.M.;Bennett,J.M.;Grose,R.W.;Cohen,J.P.;Patton, R.L.;Kirchner,R.M.;Smith,J.V.Nature,1978,271:5121223。
三维Biot固结理论的一种张量形式有限元算法
第43卷第9期 山西建筑Vol.43No.92 0 1 7 年3 月SHANXI ARCHITECTURE Mar.2017 • 83 •文章编号:1009-6825 (2017) 09-0083-02三维B iot固结理论的一种张量形式有限元算法张译心左博文(东北林业大学土木工程学院,黑龙江哈尔滨150040)摘要:基于Biot的假定,从连续介质力学的弹性方程开始,利用张量推导三维Biot本构方程,再根据Darcy定律推导出了控制方 程,并对三维Biot问题控制方程进行空间离散和时间离散,给出空间有限元格式以及时间差分格式,便于后续计算机求解。
关键词:三维Biot,Darcy定律,有限元,数值计算中图分类号:TU431 文献标识码:A〇引言Biot固结理论是岩土工程力学领域中的重要课题,是研究饱 和土体的目前公认的流固耦合机理的理论基础。
流固耦合分析 是进行土工,特别是土与结构相互作用问题、开挖与填筑的施工 过程的模拟等问题深人研究的主要途径与发展方向[1]。
张量理 论是解决建筑学和岩土力学的一个有力的数学工具。
自1941年,Biot[2]首次提出基于严格固结机理推导的能准确s i j= D i ju(T U其中,为弹性系数,满足式(5)。
i = j = k = l⑷(5)反映孔隙压力消散与土骨架变形之间耦合作用的真三维固结理 论以后,许多学者对这些方程进行了研究,并利用该理论解决了 大量的岩土工程问题。
国内相关文献所介绍的Biot固结理论一 般都属于Biot( 1941)提出的形式,但是以张量形式推导的很少,更重要的是近年鲜有专门研究其有限元方程形式的文献。
本文 从连续介质力学的弹性方程开始,利用张量推导三维Biot本构方 程和控制方程,为之后的计算机计算求解提供理论参考。
^0, other其中,£■,分别为杨氏模量,剪切模量,Poisson比,由于各向 同性的基本假设,它们只有两个是独立的,并满足:C= 2(二)。
CoilDesigner
CoilDesignerA Refrigerant-to-Air Heat Exchanger Simulation and Design Tool withIntegrated Multi-Objective Optimization RoutinesCoilDesigner is a flexible, user-friendly software tool that was developed to assist in the design, simulation, and optimization of air-to-refrigerant heat exchangers used in heat pumping, air conditioning, and refrigeration systems, as well as applications like automotive radiators, and water coils for fuel cells. CoilDesigner was developed by students and faculty from the Center for Environmental Energy Engineering at the University of Maryland under the Integrated Systems and Optimization Consortium (ISOC). The development has taken place through numerous research projects supported by a diverse group of multinational stakeholders.CoilDesigner is a highly customizable tool with extensive capabilities for simulating tube-fin, micro-channel, and wire-fin heat exchangers of different geometries. One of the greatest benefits of CoilDesigner is its flexibility to model virtually any tube circuitry, including both merges and splits. The user friendly interface allows a user to connect tubes on-screen via consecutive mouse clicks. The software also supports multiple fin types and fins with holes. The number of tube rows and columns that the software can model is limited only by available computer memory. CoilDesigner’s solver analyzes a heat exchanger in a tube-by-tube fashion, where each tube is subdivided into as many segments as the user desires. Furthermore, in any segment where a flow regime change takes place, additional refinement of that particular segment is automatically performed by the software to identify the transition point. CoilDesigner provides built-in options for a user to automatically generate common coil circuitry, or to save any particular geometry in a template file for later use.When simulating the performance of a coil the user has the option to impose either a mass flow rate boundary condition, which tends to solve very quickly, or a pressure boundary condition, which requires more solution time but accounts for unequal refrigerant distribution in the various circuits. Additionally, the user has the option to account for 2-dimensional air side inlet flow distribution in three variables (velocity, temperature, and humidity) to simulate uneven loading that may be caused by a fan or other flow conditions.The ISOC software team provides ongoing development, support, and technical assistance for CoilDesigner. The software is updated continually with the latest heat transfer, pressure drop, fin efficiency, and void fraction correlations available from the literature. Over 30 such correlations areCEEE is a community of innovative and forward thinking students, faculty, staff, and visiting engineers at the University of Maryland who are dedicated to:• Researching energy conversion systems ofminimum impact to the environment and greatest benefit to society.• Educating the next generation ofengineering professionals• Developing innovative solutions to currentand emerging energy conversion challenges • Developing knowledge in support ofstrategic technology decisionsThe Integrated Systems OptimizationConsortium (ISOC) at CEEE specializes in the research and development of software for modeling and optimization of energy conversion systems.CoilDesigner Screen Shotpresently implemented, and CoilDesigner supports the ability for a user to define and employ custom in-house or proprietary correlations. The interface also incorporates an option to apply appropriate correction factors to the built-in correlations to provide a closer match between predicted results and experimental data. Within the CoilDesigner platform the user has the ability to perform parametric analyses on coil geometries and operating conditions by varying coil dimensions such as tube diameter and length, fin spacing, and by varying refrigerant or air inlet parameters. This feature gives the designer an ability to investigate coil performance and sensitivity to different environmental conditions and to different manufacturing options. CoilDesigner also incorporates built-in and user defined cost functions, which help to capture the economic impact of engineering decisions when designing a coil. Detailed results of parametric studies can be viewed and plotted within the program, and can be exported to a spreadsheet or optionally in formatted text.One of the premier features of CoilDesigner is the integrated multi-objective optimization routines that have been built-in to the software. CoilDesigner has the ability to perform optimization on continuous variables such as tube length or fin spacing, or on discrete variables such as tube diameters, which are typically available in a limited number of sizes. Discrete optimization is implemented in CoilDesigner through the use of genetic algorithms. Figure 1 shows the results of an optimization study that was completed on a condenser. The objective of the study was to maximize heat load and minimize coil cost relative to a baseline coil. The results of a multi-objective genetic algorithm optimization lead to a set of optimum values known as Pareto Solutions, shown as red dots in Figure 1. The pink dot represents the baseline coil. Throughout the development of CoilDesigner, extensive efforts have been taken to validate its prediction capabilities against experimental data. Figure 2 shows the results of a validation study for an indoor heat pump coil used in both heating and cooling modes in two different systems. All of the predicted data, with exception of only two points lies within ±5% of the experimental results. Similar studies have been completed, and continue to be performed, for different coils and operating conditions, all with comparable results.CoilDesigner provides a well integrated, experimentally validated toolbox with a user-friendly interface for designing, simulating, and optimizing the performance of air-to-refrigerant heat exchangers for use in heat pump, air conditioning, and refrigeration systems, as well as applications like automotive radiators, and water coils for fuel cells.Figure 1. Results of a Condenser Optimization Study.0.750.80.850.90.9511.051.10.650.750.850.95 1.05 1.15 1.25 1.35Cost (Normalized with respect to baseline coil)H e a t L o a d (N o r m a l i z e d )。
LEVAPOR - DESIGN MANUAL
Dr. Imre PascikBIOTREATMENT OF WASTEWATERbyLEVAPOR BIOFILM TECHNOLOGIESMANUAL FOR PLANT DESIGNLEVAPOR GmbH, Leverkusen 2014. AprilS tructureIntroductionActivated sludge technologyBiotreatment of industrial wastewaterProblems at biotreatment of industrial pollutantsImmobilisation of biomass, requests on optiized carrierLEVAPOR carrier: attributesEffects of LEVAPOR carrier on aerobic and anaerobic bioprocessesDesign of LEVAPOR supported biotreatment plants∙Biokinetics : degree of degradation, reaction velocity, loading rates,∙Aeration, fluidization∙Carrier retention∙Generation and separation of excess sludgeProcess economyINTRODUCTIONPorous, adsorbent, LEVAPOR biocarrier represent an special type of high performance carrier materials for microorganisms, created and developed onbasis of various scientific and practice oriented requirements.LEVAPOR carrier comprise of flexible, porous polymeric foams, coated withsurface active, adsorbent pigments, giving the material new attributes, essentialfor their practical application, completed with a final dimensions and shape ofthe product, optimized for an energy saving aeration and fluidization.The optimized biophysical attributes and extremely high surface enable a significantly lower degree of reactor filling of only 12 to 15 vol. % instead of40 to 60 % for classical alternative plastic carriers.Due to the new carrier type, but also to a different approach to solutions of wastewater problems, a manual about LEVAPOR carrier and their applicationseems to be useful. THE ACTIVATED SLUDGE TECHNOLOGYThe biotreatment of mechanically pretreated municipal sewage, containing primarilyeasy biodegradable pollutants, in large, flat basins by aeration in presence of 3 to 4g/L active microbial flocs (“activated sludge”), represents since more than100 yearsthe most widespread technology for their treatment.Because of their similar composition, results and experiences from a bio-treatmentplant can be easily transferred and used for the design of other plants.From the other side, industrial effluents are contaminated with various, industry-specific pollutants of differing chemical structure, biodegradability and solubility,making them often slowly or non biodegradable (color, additive, etc.), but sometimesalso toxic.Fig. 1 Untreated industrial effluentsThe above mentioned attributes of pollutants as well as understanding daily fluctuatingflow of various industrial effluent streams are essential for the technology and designof plants for their treatment. While∙Design of sewage treatment plants are basing usually on the number of population and water consumption,∙Design of industrial treatment plants require still serious preliminary work, as well as practice oriented research and test work, in order to achieve optimizedtailor-made-solutions,∙where high removal of pollutants and stable process represent the main targets. DEVELOPMENT OF BIOTREATMENT PROCESSESEarlier also industrial effluent treatment plants had been designed on basis ofprinciples as applied to municipal plants, however due to different chemical structureof their pollutants (“COD” and “BOD”) , usually with quite moderate performance.After the recognition that it was not the right way, the industry has started toinvestigate mechanisms and biodegradation pathways of main industrial pollutants.We have started in the seventies with scientific studies on pollutant biodegradation and bioprocess optimization, as well as with design of innovative bio-treatment technologies for several industries, like∙Chemistry, agrochemistry and pharmaceuticals,∙Fermentation industries (yeasts, antibiotics, enzymes)∙Petrochemistry and refineries,∙Coal conversion technologies (coking plants, coal gasification)∙Pulp and paper, textile and at least∙Food and beverages: sugar mills, breweries, etc.FACTORS OF SUCCESSFULL BIODEGRADATIONSummarizing our experiences gathered in numerous studies on different pollutants andeffluent streams, a successful degradation of defined pollutants depend primarily onseveral essential factors:Chemical structure of pollutants –organic acids, alcohols, aldehydes, amines areeasily degradable,while pollutants containing two or more substitutes in their molecule(methyl-, halogene- or nitro groups) show remarkably slower degradability. Structuremay decrease solubility, respective bioavailability of the molecule, hindering microbialattacks, but also inhibiting the degradation process.Waste water matrix- concentration and quality of all organic and inorganic pollutants doinfluence composition of special biomass placed in sludge flocs, while increasingsalinity lowers food uptake of biomass.Microbial strains ,primarily mixtures of single strains relevant for degradation of certainpollutants must be present in required quantity in the bioreactor. They show often slowgrowth rates and week flocculation, resulting in their wash-out from bioreactor and inunstable bioprocesses.Milieu conditions - pH, temperature, aeration, redox potential, etc. are also essential formicrobial activities, which can be achieved by optimized bioreactors.Applying methods of modern biotechnology even “non degradable” pollutants can bedegraded biologically both in laboratory and also in practice.Immobilisation of biomass Retention and protection of relevant active microbial strains is essential for the stabilization and performance of the bioprocess.In the past several efforts had been undertaken, focused primarily on increase ofsludge concentration within the reactor by immobilization, microbial colonization ofsolid surfaces placed inside of the bioreactor under building of biofilms,cell agglomerates up to 20 time resistant against disturbing, inhibitory effects than suspended single cells.For long time the offered surface was the main factor of carrier efficiency, however later investigations pointed at significant importance of some other factors, especially in thebio-treatment of industrial effluents. Our R&D project on biofilm technologies we have started with tests for designingnew, optimized biocarriers, by defining attributes of ideal carriers and their effects(Tab. 1).Due to test results, the best retention of specialized biomass in bioreactor and theirprotection from toxic, inhibitory effects has been achieved by fixation of microbial cellson adsorbing, porous carrier, generating highly active biofilms resistant to inhibitorsand enabling stable processes (Fig. 2+3). Positive effects of this method have beenproven by adequate biotests under aerobic and anaerobic conditions.LEVAPOR carrier comprise of flexible, porous polymeric foams, coated with surfaceactive, adsorbent pigments, giving the material new attributes, essential for theirpractical application, completed with a final dimensions and shape of the product,optimized for an energy saving aeration and fluidization.ATTRIBUTE EFFECT1. High adsorbing capacity - binding toxic pollutants- fast colonisation+biofilm- fast startup at high level2. Porosity, high inner surface - protection of the biofilm(high biomass content) - high space-time-yields3. Fast wetting - homogene fluidisation4. Water binding - mass transport, bioactivity5. Proper fluidisation - lower energy consumption for reactor agitationTab. 1. Requests on ideal biocarriersFig.2. LEVAPOR-carrier , 20x20x7 mm delivery formFig.3 LEVAPOR-carrier: cross section (left) and colonised by biofilm of anaerobic bacteriaATTRIBUTES AND EFFECTS OF LEVAPOR ON BIOPROCESSES At least a synthetic carrier with following attributes was proven as the optimal one:ATTRIBUTE LEVAPORDimensionsSurfacePorosityWetting timeWater uptakeIonic chargeMicrobial colonisation time Recommended degree of reactor filling Full fluidisation gas upflow velocity Carrier retentionRecommended aerationExcess sludge removal - 20x20x7 mm- > 20.000 m²/m³- 90 to 95 %- immediately / 1- 2 days - up to 250 %- + to -- within 120 min.- 12 to 15 vol. %- 5 to 7 (m³/m²x h)- via 8-10 mm sieves- fine bubble aeration preferred- by fluidizationTab. 2. Physico-chemical properties of LEVAPOR carrierBy coating with up to 50% of powdered activated carbon, physico-chemical attributesof PUR foam cubes were changed significantly, their hydrophilicity, adsorbingcapacity, water uptake and density increased (Tab. 2.) enabling them better propertiesduring their application. The performance of biofilms fixed on LEVAPOR-biocarrier has been investigated atseveral laboratories under aerobic, as well as anaerobic conditions, using primarilyquite “problematic” substrates.1000 mg/L (7,8 mMol) of toxic 2-Chloroaniline (2-CA) underwas carried out in parallel batch tests (Fig.4) . LEVAPOR led to adsorption of 2-CA on carrier surface and reduced its concentration(and toxicity) in liquid phase within 2 hours to 3,2 mM, enabling start and a quantitative biodegradation within 240 hrs of 2-CA including also the adsorbed fraction, indicatedby release of Cl- ions.Due to high adsorbing capacity and porosity of LEVAPOR carrier∙hazardous, inhibiting pollutants became adsorbed on carrier surface,resulting in remarkably lower inhibitory effects in the liquid phase and∙faster microbial colonisation and generation of active biofilm takes place,resulting in∙higher resistance of microbial cells in biofilm against toxic effects, ∙higher process performance; degradation of adsorbed pollutants and∙biological regeneration of adsorbing capacity of LEVAPOR (fig. 4).suspended and on LEVAPOR fixed microorganisms 1( 1Prof.Streichsbier, et al., University of Vienna, Austria)NITRIFICATION,the key reaction of nutrient removal process is often unstable, because of ∙Slow growth and low cell yield of nitrifying microorganisms, allowing their wash-out of the bioreactor and∙Their remarkable sensitivity to- changes of pH, temperature and salinity, respectively- organic and inorganic inhibitors, resulting in reversible orirreversible inhibition of the process.Due to their high adsorbing capacity and porosity, LEVAPOR carrier do support nitrification by two parallel mechanisms:∙Fast microbial colonisation and biofilm generation result in - higher resistance against inhibiting effects and- higher process performance, while their∙High adsorbing capacity does reduce the inhibiting effect and enables a fast biodegradation of inhibitors.Nitrification of industrial effluentsmay be problematic, because of inhibitory effects of several organic pollutants and salinity fluctuations. Increase in salinity results in decreased uptake of organic pollutants and especially nitrogene, meaning lower degrees of COD- and N-elimination. Presence of even low concentrations of special inhibitors results often in a crash of nitrification process even under continued non inhibited COD-removal.Via immobilisation of nitrifying biomass, negative effects of inhibitors can be reduced remarkably (Fig. 5, right: 94,5 % nitrification, versus only 28% achieved by suspended biomass, left). Both, higher resistance and higher number of microbial cells fixed on carrier do contribute to stability of the process.Fig.5 : Effect of biomass immobilisation on nitrification of saline and inhibiting chemical effluents (salinity:20-25 g/L,COD~1600mg/L) at Lv~ 0,25gN/Lxd.Nitrification of municipal sewageNitrifying bacteria are growing and sedimenting slowly, flocculating weakly and not tending to be integrated into sludge flocs, resulting often their wash-out from the aerated basin and respective basins with long retention times or their remaining there. Nevertheless, in a field test in Finnland it has been proven, that by adding 12 vol.% of LEVAPOR into a basin designed for BOD-removal, within 3 weeks a stable nitrification has been established at low temperatures (Fig. 6.)Fig. 6. Establishment of nitrification within 4 weeks in winter in afluidized bed reactor upgraded with 12 vol.% LEVAPOR20719514910suspended biomassimmobilised biomassinletoutlet28 %94,9 %Simultaneous denitrification under aerobic conditionsAs result of high porosity and inner surface of LEVAPOR carrier as well as lower redoxpotentials inside the cubes, during the nitrification in presence of LEVAPOR, usually a simultaneous aerobic denitrification appears (Fig. 7), typical primarly for porous carrierlike LEVAPOR.Fig.7 Outlet-NH4N and -NO3N during the nitrification of sewage (lab test) Those results have been reproduced and confirmed also in a full scale municipal plantusing LEVAPOR biocarrier (Fig. 8)Fig. 8 Simultaneous nitrogen removal in the NINGAN (North-East-China) full scale plant, Dec. 2012 - Nov. 2013Biodegradation of industrial pollutants under anaerobic conditionsSimilar positive effects of LEVAPOR have been confirmed also in biotests under anaerobic conditions, for degradation of 2-Chlorobenzoic acid (2-CBA), a quite strong biocide, using methane production as indicator of degradation. While non-modified-PU-foam or sinterglass carrier showed only small effects with slow generation of methane, achieved the anaerobic reactor with LEVAPOR within few days after startup a remarkable biogas production, completed within 18 to 20 days(fig. 9).Fig. 9 Effect of carrier type on biodegradation of 2-Chlorobenzoic acidunder anaerobic conditionsAnaerobic- aerobic treatment of toxic pulp mill effluentsDue to the generation and enrichment of toxic intermediates in the medium under aerobic conditions, biotreatment of several complex organic pollutants by activated sludge method shows only moderate results, while anaerobic treatment achieves remarkably better results.Aerobic treatment of pulp mill bleaching effluents containing toxic chloroorganic pollutants, achieved only 35 to 40 % COD removal, however anaerobic biofilms fixed on adsorbing, porous carrier 65 to 70 % (Fig. 10)and due to a remarkable conversion of pollutants, further 45 to 60 % of the residual COD has been removed in the following aerobic post-treatment step. Thanks application of 12 vol.% adsorbent carriers in anaerobic reactors, their total volume could be reduced from the initially planned 65.000 m³ (UASB-system) to only 18.000 m³ for the biotreatment of 10.000 m³ toxic pulp bleaching effluent, loaded with 45.000 kg/d COD (Fig. 11).Regarding LEVAPOR applications so far, the addition of 12 to 15 vol.% carrier into the bioreactor resulted in average in a doubling of the plant performance, a higher process stability and a lower excess sludge generation.Fig. 10. Anaerobic treatment of toxic pulp mill bleaching effluents by biofilms fixed on different carrier material: 1. LEVAPOR 2. Activated carbon3. PU-foam and4. suspended biomass as controlFig. 11 Biotreatment plant for toxic pulp mill effluents by LEVAPOR technology DESIGN OF LEVAPOR SUPPORTED BIOTREATMENT PLANTSThe BIOREACTOR DESIGN comprises ofREACTOR LAYOUT - basing on volumetric loading ratesCARRIER RETENTIONAERATION AND AGITATION andSLUDGE SEPARATIONThe PLANT DESIGN starts with the LAYOUT of BIOREACTORS resp. their VOLUMESbased on biokinetic data of a given process, determineda) via practice oriented continuous lab, or on-line pilot tests , carried out direct atproduction site (recommended especially for industrial effluent treatment plants)and/orb) on basis of results obtained in the treatment of similar effluents and sewage. Provider of plastic carrier, recommend process design on basis of the surface loading of carrier materials.However, due to the high surface and porosity, as well as adsorbing capacity, for LEVAPOR other, practice relevant parameter should be taken in account :AERATION OF FLUIDISED BED BIOREACTORSTarget: oxygene supply for microorganisms andagitation of the medium, achieving masstransfer of O2+pollutants to biofilm.Recommended type of aeration for LEVAPOR carrier1. Recommended is fine bubble aeration , via1.1. Porous, flexible membranes (discs or pipes, fig. 11)1.2. Ejectors : until 6-8 m water depth and1.3. Injectors : up to 15 -20 m water depth2. Surface aerators - carrier cubes should be put inadequate cage with 10 mm meshfor protection of mechanical damage.Fig. 11 Membrane disc aeratorsIn the full scale plant in Finnland the fluidising behaviour of colonised carriers in the reactor was studied by determining the carrier density (cubes/L) in the reactor as a function of air flow . Carrier density was determined three times, approximately once a month and all tests gave similar results. The highest density as a function of air flow was found at 6 to 7 m³ / m² basin surface per hour, however the density measurements were made only from samples taken from the water surface, so any possible density gradient toward the bottom could not be perceived. When the air flow per basin area fell below 4 m³/m² x h , carrier density began to drop substantially.Fig. 12 Effect of aeration density on fluidization of colonized carrier:In municipal plants aeration for pollutant removal is enough! RETENTION OF THE CARRIERThe LEVAPOR biofilm process uses cubes of 20 * 20 * 7 mm size , which has been chosen to enable their easy retention in the reactor. The simplest separation method of colonized carrier cubes from the treated wastewater-cell-suspension is their filtration through a screen with 8 to 10 mm mesh openings or through adequate strainer, however at upgrading of existing plants their design and dimensions must be adapted to the design of available basins.Basic principle - in order to avoid clogging of the separating surface, it is important to choose flow velocities through the filter area remarkable lower than through the outlet pipe , meaning to design a remarkable higher filter area ( 3 to 5 x >) than the cross section of the outlet pipe.Materials – with regard to eventually corrosive wastewater, carrier separator should be made of non corroding materials, like stainless steel or adequate plastic materials. Forms – there are three main types,∙screen plates installed at inner wall side of a longitudinal b,asins∙screen baskets (like a half wastepaper basket) for round reactors and∙perforated pipes , installed in the mid or at inner side of round, rectangular, but also longitudinal basins.Fig. 13. Possible carrier retention in cylindrical and longitudinal reactorGENERATION AND SEPARATION OF EXCESS SLUDGEDue to the longer sludge retention times (“sludge age”) , respectively longer oxidationtimes, biofilm systems generate usually lower quantities of compact excess sludge.The removal of excess sludge from the carrier surface occurs via fluidisation of thecarrier bed, because only living cells are able to be integrated into the biofilm structure,while dead and excess sludge cells will be released spontaneously from the biofilm.The cells released from the carrier surface leave the reactor through the screen andoverflow, arriving to the clarifier, where they will settle in several types of usualgravitational separation devices, like conic, longitudinal or pipe shaped clarifiers, etc. PROCESS ECONOMYThe main target of every biotreatment process is the highest possible removal ofpollutants at lowest possible costs, what can be achieved by application of new, highlyefficient processes with low capital and operation expenses, especially via- high space-time-yields- high process stability- low energy consumption- minimized generation of secondary products (excess sludge) and- low investment costs and- low maintenance costs.Most of the mentioned advantages can be reached by biofilm technologies, especiallyby using LEVAPOR biocarrier. Following casa histories will confirm this advantages:a. Anaerobic-aerobic treatment of toxic pulp mill bleachning effluents in GermanyThe originally proposed aerobic treatment achived only 35 to 40% COD-removal,because of generation of inhibitory metabolites, while the anaerobic process achieved60 to 75%,plus ca.50% removal of residual COD in the aerobic posttreatment step.For the anaerobic treatment of a daily load of 45 tons COD, UASB reactors of 65.000 m³have been offered, using LEVAPOR carrier this volume has been reduced to 18.000 m³,meaning 47.000 m³ less anaerobic volume !b. Upgrade of a municipal sewage treatment plant (STP) for nitrification (Finnland)In a sewage treatment plant designed for BOD removal, years later nitrification wasrequired. Instead of usually practicised doubling of reactor volume, into the aerobicbasin 12 vol.% LEVAPOR carrier were added. Within 3 weeks a stable nitrification hasbeen established, enabling significant cost savings ( investments of 75 EURO/m³ forLEVAPOR, instead of 300 EURO/m³ of aerated basin, complete) but also time savings.c. Municipal sewage treatment plant with higher loading rates (China)Based on above described experiences, in China a new STP for 22.000 m³/d sewagewas designed with only 3,8 hrs. hydraulic retention time in the aerated basin.The plantachieves ca. 90% COD, BOD and NH4N+ removal, denitrifying further under aerobicconditions ca. 50 to 60% of the generated NO3N.d. Significantly lower LEVAPOR fillingDue to high active surface and adsorption capacity, the required reactor filling of LEVAPOR carrier is in the range of only 12 to 15 vol.%, compared with 40 to 65 % for plastic carriers, meaning significant economic advantages over them.Additionally to lower expenses for carrier material and their shipment costs, application of LEVAPOR biocarrier results also further advantages, like lower energy consumption for agitation and aeration.Our experiences in biotreatment of complex, industrial effluents include ∙Petrochemistry∙Chemistry and pharmaceuticals∙Pulp and paper∙Landfill leachates∙Steel works, coal gasification, coke plants, etc∙Textile and leather industryOur services for youwe do offer also our services in designing taylor made problem solutions,based on 40 years experiences on biofilm technologies and nutrient removal, both in the field of science and in the practice. Our tools are:∙Analysis of the problem∙Elaboration of alternatives for problem solution , supported by∙Practice oriented biotests (especially for nitrification),∙Process Design and/or Engineering∙Production and delivery of the required LEVAPOR type and∙Plant startup using optimized mixed biomass, enriched with microbes essential for degradation.。
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ISPE HVAC(翻译版)国际制药工程协会对空调系统的基准指南
聚二甲基硅氧烷芯片自由酶反应器检测葡萄糖
聚二甲基硅氧烷芯片自由酶反应器检测葡萄糖仲海燕;周洁;余晓冬;陈洪渊【期刊名称】《分析化学》【年(卷),期】2010(38)6【摘要】应用电泳中介微分析(EMMA)技术,构建聚二甲基硅氧烷(PDMS)芯片自由酶反应器, 在线检测葡萄糖(Glu),在十字形的芯片通道上,采用自制的碳纤维微电极检测葡萄糖氧化酶(GOD)催化氧化Glu生成的H2O2,并对检测电位、GOD浓度、GOD进样时间、分离电压等参数进行了优化,测定了该自由酶反应器的线性范围和检出限,考察了其重现性及稳定性.结果表明,此自由酶反应器制作方便,操作简单,重现性好,Glu浓度在0.1~20 mmol/L之间有较好的线性关系(r=0.997),检出限为19.8 μmol/L(S/N=3).【总页数】4页(P767-770)【作者】仲海燕;周洁;余晓冬;陈洪渊【作者单位】南京大学化学化工学院,生命分析化学教育部重点实验室,南京,210093;南京大学化学化工学院,生命分析化学教育部重点实验室,南京,210093;南京大学化学化工学院,生命分析化学教育部重点实验室,南京,210093;南京大学化学化工学院,生命分析化学教育部重点实验室,南京,210093【正文语种】中文【相关文献】1.葡萄糖氧化酶修饰聚二甲基硅氧烷-纳米金电极的制备及其应用 [J], 王伟;毕连花;唐帆2.PDMS芯片自由酶反应器检测葡萄糖 [J], 仲海燕;周洁;余晓冬;陈洪渊3.PDMS芯片自由酶反应器检测葡萄糖 [J], 仲海燕;周洁;余晓冬;陈洪渊4.微型HPLC-固定化酶柱后反应器-电化学检测法测定血清和全血中的葡萄糖 [J], 邹公伟;文红梅5.用微芯片化学反应器实现酶催化化学发光测定葡萄糖的研究 [J], 徐溢因版权原因,仅展示原文概要,查看原文内容请购买。
二级连续系统混合培养益生菌及
二级连续系统混合培养益生菌及纤维益生菌片的研制薛胜平1,2,杜连祥2,路福平2(1.河北经贸大学生物科学与工程学院,河北 石家庄 050061;2.天津工业微生物重点实验室,天津科技大学生物技术学院,天津 300457)摘 要:将填充床固定化系统连于单级液态连续培养系统后构建二级连续培养系统,接种肠膜芽孢杆菌、双歧杆菌与酪酸菌、嗜酸乳杆菌、粪肠球菌,运行12d 、三个批次,未出现污染、堵塞现象,五种益生菌固相总生物量高达3.5×1010/g。
连续混合培养五种益生菌,菌密度高,菌与纤维载体不需分离,经干燥、干法压片得到了纤维益生菌片,产品活菌数为109/g,高出国家标准1000倍。
关键词:固定化;连续培养;混合培养;益生菌;纤维益生菌片Two Stages Continuous Fermention Process of Five Probiotic Bacterial Strains for Fiber Embeded Probiotic TabletsXUE Sheng-ping 1,2,DU Lian-xiang 2,LU Fu-ping 2(1.College of Biosicence and Bioengineering, Hebei Economic and Business University, Shijiazhuang 050061, China;2.Tianjin Key Laboratory of Industrial Microbiology, College of Biotechnology, Tianjin University of Science and Technology,Tianjin 300457, China)Abstract :Five strains of probiotic bacteria were fiber embeded and cultured in a continuous fibrous bed bioreactor with cornfiber as the carrier. The immobilized biomass was studied by selective culture methods. Bifidobacterium longum TQ21-2-2,Lactobacillus acidophile CICC06005, Clostridum butyric TO-A, Bacillus mesentericus TO-A and Enterococcus faecalis T-110were found to have coexisted stably. The total biomass of five probiotics in immobilized phase was 3.5×1010 g in corn fiber of the fibrous bed bioreactor. The system can be used to obtain formulation of microecological and fiber embeded tablets, so as to produce solid high biomass commensal probiotics products continuously. The fiber and bacteria were dried into functional food tablets with probiotics biomass in the amount of 109/g, 1000 times higher than that estimated in China national standard.Key words :immobilization ;continuous culture ;mixed culture ;probiotics ;food tablet中图分类号:TS261.1.6 文献标识码:A 文章编号:1002-6630(2008)05-0265-04收稿日期:2007-04-04作者简介:薛胜平(1962-),女,高级工程师,在职博士研究生,主要从事微生物学与生物化学工程研究。
与基质芯片相关的方法和组合物[发明专利]
专利名称:与基质芯片相关的方法和组合物
专利类型:发明专利
发明人:安德鲁·J·曼尼托斯,罗伯特·弗伯格,卡拉·瓦尼纳吉申请号:CN200480037140.0
申请日:20041013
公开号:CN101389753A
公开日:
20090318
专利内容由知识产权出版社提供
摘要:本发明涉及用于评估细胞间和细胞与基质材料间相互作用的设备和方法,其中由于这些相互作用形成的细胞分布模式是对细胞入侵潜能的指示物。
此外,这些设备和方法可以提供对入侵性细胞转移的优选位点的指示;对使用到这些细胞上的抗癌药物的功效的指示;以及对试剂促进或提高肿瘤生长或转移的潜能的指示。
申请人:伊利诺伊大学评仪会
地址:美国伊利诺伊州
国籍:US
代理机构:北京金信立方知识产权代理有限公司
代理人:黄威
更多信息请下载全文后查看。
Stora Enso公司新的生物质材料创新中心在斯德哥尔摩举行落成典礼
worldwide news 环球纸业欧洲造纸工业联盟(CEPI)近日表示,对欧洲委员会(European Commission,简称欧委会,是欧盟(European Union)的行政机构)于2015年12月提出的循环经济方案表示欢迎。
“我们已经达到预期。
这项重要的政策意图恰如其分地指出了真正的解决方案所需要的协同效应。
这一方案表明了非常大的决心,而这在以往的政策制定中非常少见。
”CEPI总干事Marco Mensink表示。
在确认了生物质资源以及生物质基产品对循环经济的贡献之后,欧委会开始考虑在多个以可再生资源为原料的行业中实施循环经济方案。
CEPI期待在生物质基产品领域的具体行动。
此外,虽然处理废物管理权尚未给欧洲创造价值,但欧委会已经认识到其重要性。
“很高兴看到欧委会认识到对纸张进行分类收集的必要性,这可以为纸厂提供优质原料,”Mensink说道,“我们也非常高兴地看到,对垃圾填埋的进一步限制措施在一些地方已经落实到位。
这体现了行业需求和许多其他利益相关者的一致性。
关于这一点,欧委会做出了明智的决定,应该尽快从立法层面落到实处。
”CEPI同样相信,在可再生资源利用对防止废物产生起到的作用,以及协调修正再循环率的计算方法以确保数据更具可比性和可信度方面,欧委会的认识是正确的。
欧洲造纸行业及整个造纸产业链的相关伙伴将出版欧洲纸张循环宣言,争取将欧洲纸张回用率在目前71.7%的基础上再进一步提升。
(石 瑜)Stora Enso公司新的生物质材料创新中心的开幕典礼于2015年12月17日举行,瑞典企业与改革事务大臣Mikael Damberg和Stora Enso公司CEO Karl-Henrik Sundström一同出席了开幕典礼。
新落成的生物质材料创新中心将承担研究、应用、商业开发以及战略营销等多项职能。
以木材等第二代生物质材料为原料,获得可再生能源产品及解决方案,从而替代现有的化石基能源产品。
Bioreactor
专利名称:Bioreactor发明人:HUGEL, JOERG,SCHOEB, RETO申请号:EP10183802.7申请日:20000818公开号:EP2290050A1公开日:20110302专利内容由知识产权出版社提供专利附图:摘要:The hollow fiber bioreactor comprises a reaction container (1e) for a good to be subjected with a medium and a pump (5e) by which the medium is conveyed. The pump for conveying the medium is formed as single pump and/or part of the pump is formed as single part. The reaction container comprises a flexible bag (10e), which is insertableinto a form-stable reception. The medium is conveyed through a feed line (2e) in the reaction container. The rotor of the pump is arranged within the reaction container. The pump and/or the pump part is produced from plastic. The hollow fiber bioreactor comprises a reaction container (1e) for a good to be subjected with a medium and a pump (5e) by which the medium is conveyed. The pump for conveying the medium is formed as single pump and/or part of the pump is formed as single part. The reaction container comprises a flexible bag (10e), which is insertable into a form-stable reception. The medium is conveyed through a feed line (2e) in the reaction container. The rotor of the pump is arranged within the reaction container. The pump and/or the pump part is produced from plastic. The pump wheel and the reaction container are formed as single part. The pump comprises pump housing, in which the pump wheel is arranged, and/or a separate drive stator, in which the pump housing is inserted with the pump wheel. The pump wheels are formed as permanent magnet and the pump is formed as gear pump. The bioreactor is formed as bubble reactor having a reaction container, in which the hollow body is arranged, whose cover is connected at its lower end with the wall of the reaction container and which rejuvenates itself in the direction to the upper end of the reaction container so that it subdivides the interior area of the reaction container into an upper chamber and a lower chamber. The upper and lower lateral surfaces of the hollow body are formed in gas- and fluid permeable manner. The goods to be subjected are arranged in the hollow area. The feed line flows for the fluid medium in the upper chamber and a suction device is arranged in the lower chamber for the fluid medium and/or a supply device is arranged in the lower chamber for the gaseous medium. The reaction container is cylindrically formed and the hollow body is circularly formed. The feed line flows in a ring-shaped distributor, which is arranged in the upper chamber and surrounds the hollow body. The suction device arranged in the lower chamber is formed for the fluid medium in ring-shaped manner.申请人:LEVITRONIX LLC地址:85 First Avenue Waltham, MA 02451 US 国籍:US代理机构:Sulzer Management AG更多信息请下载全文后查看。
新编文档-生物反应器课件bioreactordesignSelectcellculturemethod-精品文档
• Time • Temperature • Moisture
Air Removal
Sterility Considerations
Sterility Considerations – Killing rate
• F0 = ∫ ti * 10(Ti - 121) / Z • F0 = Integrated amount of lethality delivered
Temperature control
Cooling System: • remove 50 to 100 Watts/Liter of Volume.
Heating Systems: • One (1) degree C per minute between 25 and 45 C
Ring Type
during a cycle i.e. A cycle with F0 = 17 minutes has a lethality equivalent to 17 minutes at121 C.
CIP considerations
• Sterile Piping should be pitched for drainability. • CIP Fluids
Bioreactor design considerations
Goals: Max growth or max productivity
• Need stringently maintained process conditions • Agitation (max transfer) • Homogenous condition
Bioreactor design
Select cell culture method
Design Building Life
Design Building Life无【期刊名称】《微型计算机》【年(卷),期】2014(000)008【摘要】画图神器:Accutrax铅笔小伙伴们不用猜了,这把长得像美工刀的家伙其实是一种画图铅笔!美国制造的Accutrax铅笔,突破传统铅笔芯的圆柱形状,摇身一变为刀片。
此笔不但可以像美工刀那样伸缩自如,用碳纤维进行加固的“刀笔芯”也如刀片般坚韧,不会轻易断掉,并且还有彩色的可选。
从此再也不需要花时间去削尖铅笔了,画图狗们值得拥有啊!【总页数】2页(P8-9)【作者】无【作者单位】不详【正文语种】中文【中图分类】TS951.12【相关文献】1.Towards Climate Responsive Building Design: Bio-Climatic Design Features of Residential Building Typologies in the Warm-Humid Climate of Ghana [J], Samuel Amos-Abanyie;Kwabena Abrokwa Gyimah;Eunice Akyereko Adjei2.Application of Green Building Design in Residential Buildings [J], Wen Zhang3.Seismic hazard level reduction for existing buildings considering remaining building lifespans [J], Ji-Hun Park4.Estimation of Building’s Life Cycle Carbon Emissions Ba sed on Life Cycle Assessment and Building Information Modeling: A Case Study of a Hospital Building in China [J], Kun Lu;Hongyu Wang5.Energy Assessment of Building Integrated Photovoltaics and Fuel Cell Systems: Design Study for Building(s) of Mie, Japan [J], Akira Nishimura;Satoshi Kitagawa;Masafumi Hirota;Mohan Lal Kolhe因版权原因,仅展示原文概要,查看原文内容请购买。
微生理系统之研究将彻底改变实验生物医学
圆满成功,我们必须整合多个技术领域,包括微 流控芯片、干细胞生物学、三维微结构/矩阵、多 细胞工程、通用的血液替代品,各种生物检测技 术和资料库工具,以及计算单一或是
多个器官系统的电脑模型。此一创举将革命性的 改变基础生物学,生理学,药理学,毒理学和药 物,以及一个新的领域:定量系统药理学,因为 反复性实验、疾病模型、药控制诱导多 功能性干细胞之专一性分化,以及人体器官间之 代谢与讯息传递的动态变化。 美国食品药品管理局国家毒理学研究中心主任, 威廉
史力克二世博士评论道:“目标是十年内完成这 个‘人体晶片’-类似1960年代人类登陆月球之 壮举,目前看来似乎不可行,但是我相信从生理/ 毒理学模拟人体反应之观点来看
今年9月,实验生物医学的年度主题将专门探讨 “微生理系统的生物医学”,并介绍由NIH的共 同基金资助的转译科学推动中心科学家所执行的 研究成果。该项目支持了来自20多
个机构,共十四个杰出研究团队发表了许多具影 响力之论文。 在2014年9月,实验生物医学的年度主题将专门 探讨微生理系统的生物医学,并介绍由美国国家 卫生研究院(N
该领域中已有许多成果发表,这些文章阐述着杰 出研究者们在实现完全整合十种器官系统为目标 下,其得到之结果与发现。而这些组织抑或是器 官芯片的应用对于未来科学应用与发现
,更是无穷无尽的。” 《实验生物学与医学》期刊主编史蒂芬古德曼博 士说道:“我们深感荣幸地能够发表这个“微生 理系统的生物学与医学”主题专刊,约翰威特斯 沃博士是值
骨和软骨,脑,胃肠道,肺,肝,微血管,生殖 道,骨骼肌,皮肤,和器官芯片之互连来进行生 理药物动力学、药物发现和筛选,以及利用微观 技术来调节干细胞分化等。 威特斯
沃博士提到创建微生理系统的最初动机是为了提 升人类相关药物之研发与测试的效率。该技术着 重应用于包括环境毒素对人类的影响,化学品及 生化武器之鉴定、定性与中和无法在人
质子导体基固体氧化物燃料电池的新认识
第49卷第1期 2021年1月硅 酸 盐 学 报Vol. 49,No. 1 January ,2021JOURNAL OF THE CHINESE CERAMIC SOCIETY DOI :10.14062/j.issn.0454-5648.20200390质子导体基固体氧化物燃料电池的新认识曹加锋1,冀月霞1,邵宗平2(1. 安徽工业大学数理科学与工程学院,光电信息材料与技术研究所,安徽 马鞍山 243032;2. 南京工业大学化工学院,材料化学工程国家重点实验室,南京 210009)摘 要:质子导体基固体氧化物燃料电池(P-SOFC/PCFC)是建立在质子传导机制上的全固态、绿色、经济的发电装置。
鉴于目前固体氧化物燃料电池(SOFC)的低温化发展趋势,本综述系统分析了PCFC 内部的质子传导机制,总结了目前常见的PCFC 电解质和电极材料,探讨了PCFC 内部质子传导通道的高效构建问题。
在材料研究方面,重点分析了各类PCFC 材料的设计理念和目前仍存在的问题。
针对PCFC 的未来发展趋势,指出开发新型的质子导体电解质和电极材料仍然是目前这一领域亟需进行的工作。
关键词:质子导体基固体氧化物燃料电池;钙钛矿结构氧化物;电解质材料;电极材料中图分类号:TK91 文献标志码:A 文章编号:0454–5648(2021)01–0083–10 网络出版时间:2020–12–17New Insights into the Proton-Conducting Solid Oxide Fuel CellsCAO Jiafeng 1, JI Yuexia 1, SHAO Zongping 2(1. Institute of Optoelectronic Information Materials and Technologies, School of Mathematics and Physics, Anhui University of Technology, Maanshan 243032, Anhui, China; 2. State Key Laboratory of Materials-Oriented Chemical Engineering, College ofChemical Engineering, Nanjing Tech University, Nanjing 210009, China)Abstract: Proton-conducting solid oxide fuel cells (P-SOFCs/PCFCs) are all-solid-state, eco-friendly, and economic power generation devices for proton conduction in oxide lattices. This review represented the proton conduction mechanism, the typical electrolyte and electrode materials used in PCFCs, and the efficient construction of the internal proton conduction pathways based on the development of low-temperature working SOFCs. The principles of designing these materials were analyzed and some possible problems in this aspect were discussed. This review also indicated the future work on PCFCs to develop some novel electrolytes and electrode materials with an improved proton conductivity.Keywords: proton-conducting solid oxide fuel cells; perovskite-type oxides; electrolyte materials; electrode materials固体氧化物燃料电池(SOFC),又名陶瓷燃料电池,是以全固态氧化物作为主要工作介质的电化学能源转化装置[1]。
新型相变型存储器研究进展
新型相变型存储器研究进展李娟1,王嘉赋1, 21武汉理工大学理学院物理科学与技术系,湖北武汉 (430070)2 材料复合新技术国家重点实验室,湖北武汉 (430070)E-mail:wuhan0602@摘要:文章系统地介绍了新型相变存储器的原理及特点、相变材料、写电流、器件稳定性和读取速度等关键性能因素以及器件结构设计和热场分布等。
CRAM的发展空间十分广阔,十分有希望成为最具有市场竞争力的新型存储器之一。
关键词:相变材料;写电流;稳定性;结构设计;热场分布1. 引言相变型半导体存储器指硫系化合物随机存储器(Chalcogenide Random Access Memory),简称CRAM,又被称作奥弗辛斯基电效应统一存储器,是基于Ovshinsky在20世纪60年代末提出的奥弗辛斯基电效应的存储器。
CRAM所采用的存储技术是一种新型的非易失性半导体存储技术,即利用相变层发生相变前后阻值的差异来对数据进行存储[1]。
它利用具有可逆结构的硫族化合物作为相变物质,利用热能所激发的相变物质所发生的快速可逆相变来存储数据[2]。
通入写电流后,由于电阻加热器的加热作用,相变层的温度迅速升高,当达到相变薄膜的熔点时,部分材料熔化,失去了晶体状态,这时快速冷却,从而将其锁定在非晶态,非晶态在接近室温时非常稳定,但是当接近融化温度时,它的晶核形成和微晶生长的速度成指数增长。
为了在冷却的时候,不使材料重新结晶,冷却的速度要比晶核形成和生长的速度更快。
为了使存储元件重新回到可导状态,材料要被加热到结晶温度和熔化温度之间,使晶核和微晶生长在几个纳秒内快速发生[3],从而使材料转变为晶态。
相变前后材料的阻值差可达到4-6个量级。
与目前已有的多种半导体存储技术相比,它具有循环寿命长、元件尺寸小、功耗低、可多级存储,制作工艺简单等优点[4-10]。
此外它的最大优势在于:该存储技术与材料带电粒子的状态无关,从而具有很强的抗空间辐射能力,能满足国防和航天需求,是目前国内外重点研制的新型存储器。
巴斯夫推出全新工程工具
巴斯夫推出全新工程工具
佚名
【期刊名称】《《轿车情报》》
【年(卷),期】2009(000)011
【摘要】9月24日,工程塑料界的巨头德国巴斯夫股份有限公司在其位于上海浦东的技术研发中心召开“巴斯夫媒体圆桌会议”,向中国媒体介绍了巴斯夫开发的虚拟汽车开发工具Ultrasim。
【总页数】1页(P219)
【正文语种】中文
【中图分类】TP18
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Biochemical Engineering Journal13(2003)113–125Bioreactor designs for solid state fermentationA.Durand∗Platform for Development in Biotechnology,UMR-INRA1082(IBQ),17Rue Sully,Dijon21065,FranceReceived17December2001;accepted after revision24July2002AbstractSolid state fermentation has gained renewed attention not only from researchers but also from industry.This technique has become a more and more attractive alternative to submerged fermentation for specific applications due to the recent improvements,especially in the design.This paper reviews the various reactor designs and focuses on the differences between lab-scale and industrial-scale designs.It highlights the main designs that have emerged over the last10years and the potential for scaling-up for each category of reactor.©2002Elsevier Science B.V.All rights reserved.Keywords:Solid state fermentation;Bioreactor design;Engineering;Scale-up strategies1.IntroductionIs solid state fermentation(SSF)a new challenge for a very ancient technology?The question is worth asking be-cause this“ancient art”is in the process of becoming a mod-ern technology.During the last10years,many articles have been pub-lished,several books have been edited showing a spurt of SSF processes even in western countries.The fact that this process is particularly well adapted to the metabolism of fungi,the micro-organisms most commonly in SSF pro-cesses,is an important feature because of the characteristics of these micro-organisms(apical growth,enzymatic ac-tivities).Moreover,in western countries,recent important problems has emerged such as:pollution of soils and the potential use of bioremediation,BSE epidemic and the ne-cessity tofind alternative for animal feeding,to cite only two examples.Thus,SSF has gained a new interest from researchers and manufacturers over the past10years. Many papers have appeared on the use of solid state fer-mentation,with studies on the effects of different factors on fungus metabolism,and the potential for producing differ-ent metabolites[1–3].The great majority of these papers were SSF processes at laboratory-scale.Conversely,very few works have been carried out on the engineering aspects and problems of scale-up.Compared to submerged fermentation,the solid media used in SSF contain less water but an important gas phase ex-ist between the particles.This feature is of great importance ∗Tel.:+33-3-8069-3061;fax:+33-3-8069-3229.E-mail address:durand@dijon.inra.fr(A.Durand).because of the poor thermal conductivity of the air compared to the water.Another point is the wide variety of matrices used in SSF which vary in terms of composition,size,me-chanical resistance,porosity and water holding capacity.All these factors can affect the reactor design and the control strategy for the parameters.Indeed in submerged fermenta-tion,we can consider roughly that all the media are made up essentially of water.In this environment,the temperature and pH regulations are trivial and pose no problem during the scaling-up of a process.In submerged fermentation,only one major difficulty is encountered:the transfer of oxygen to micro-organisms which depends upon the shape,the size of the reactor and the agitation/aeration system used.To characterise this transfer,a parameter,K L a(oxygen trans-fer coefficient),has been defined.It can be considered as a“similarity invariant”,i.e.its value expresses the capac-ity of the equipment to transfer oxygen independently of the volume of the reactor and so,constitutes an important parameter used for the scale-up studies in submerged fer-mentation.In SSF,besides the oxygen transfer which can be a limiting factor for some designs,the problems are more complex and affect the control of two important param-eters:the temperature and the water content of the solid medium.Other factors also affect the bioreactor design:(i)the mor-phology of the fungus(presence or not of septum in the hyphae)and,related to this,its resistance to mechanical ag-itation,(ii)the necessity or not to have a sterile process. Before analysing the various types of bioreactors,their advantages and drawbacks,it is important to specify that in a general way,many types of reactors are able to run at laboratory-scale with small quantities of medium.But,the1369-703X/02/$–see front matter©2002Elsevier Science B.V.All rights reserved. PII:S1369-703X(02)00124-9114 A.Durand /Biochemical Engineering Journal 13(2003)113–125scale-up is complicated mainly by intense heat generation and heterogeneity in the system [4].In this paper,emphasis will be put on the differences between bench-scale bioreactors and pilot or industrial units and also between non-sterile and sterile process.2.Bioreactor classificationTwo categories of bioreactor exist for the SSF processes:(i)at laboratory-scale,using quantities of dry solid medium from a few grams up to few kilograms,(ii)at pilot and industrial-scale,where several kilograms up to several tons are used.The first category comprises many designs,more or less sophisticated,while the second category,which is used mainly at industrial level,is markedly less varied.Within each category,some of the bioreactors can operate in aseptic conditions.boratory-scale bioreactorsSeveral types of equipment are used for SSF.Petri dishes,jars,wide mouth Erlenmeyer flasks,Roux bottles and roller bottles offer the advantage of simplicity [5,6].Without forced aeration and agitation,only the temperature of the room,where they are incubated,is regulated.Easy to use in large numbers,they are particularly well adapted for the screening of substrates or micro-organisms in the first steps of a research and development program.One of the interesting lab-scale units is the equipment de-veloped and patented by an ORSTOM team between 1975and 1980[7].It is composed of small columns (Ø4cm,length 20cm)filled with a medium previously inoculated and placed in a thermoregulated water-bath (Fig.1).Water saturated air passes through each column.This eqiupment is widely used by many researchers and offers the possibilityto Fig.1.Typical lab-scale column reactor.Several columns detailed on the right part of the figure are located in a water-bath for temperature control.aerate the culture and also analyse the micro-organism res-piration by connecting the columns to a gas chromatograph with an automated sampler that routinely samples each col-umn.This equipment is convenient for screening studies,op-timisation of the medium composition and measurement of CO 2produced.The small quantity of medium (few grams)used and the geometry of the glass column is suitable for maintaining the temperature in the reactors (the heat removal through the wall seems to be sufficient).The design of this reactor,however,does not permit sampling during fermenta-tion and so it is necessary to sacrifice one entire column for each analysis during the process.This equipment,with its advantages (forced aeration,cheap,relatively easy to use),can constitute a first step in the research.A new generation of small reactors was developed by an INRA-team in France a few years later.The first model de-veloped [8]addressed problems concerning the regulation of the water content of the medium.A second model built during 2000has been tested but has not been reported in the literature.As shown in the photograph (Fig.2),this re-actor has a working volume of about pared to the first model,the principal changes were the introduction of a relative humidity probe,a cooling coil on the air circuit and a heating cover for the vessel.These changes improved the regulation of the water content during the process.As for the ORSTOM columns,the mini-reactors are filled with a medium previously inoculated in a sterile hood.Each reactor is automatically controlled by a computer.Moreover,sam-ples can be taken by opening the cover in the presence of a flame without problem of contamination.In this type of re-actor,the temperature and the water amount of the medium can be monitored by means of the regulation of the tempera-ture,relative humidity and flow rate of the air going through the substrate layer.Different profiles for the air-inlet tem-perature and flow rate can be elaborated and generate useful information for the scaling-up studies.A.Durand/Biochemical Engineering Journal13(2003)113–125115Fig.2.Photography and schematic of a lab-scale sterile reactor.(1)Heating cover,(2)medium temperature probe,(3)stainless steel sieve,(4)air-inlet temperature probe,(5)relative humidity probe,(6)resistive heater,(7)water temperature probe,(8)massicflow meter,(9)level probe,(10)insulating jacket.Fig.3.Rotating drum bioreactor.(1)Air-inlet,(2)rotating joint,(3)coupling,(4)air nozzles,(5)air line,(6)rollers,(7)rotating drum,(8)solid medium, (9)rim.116 A.Durand /Biochemical Engineering Journal 13(2003)113–125Fig.4.Perforated drum bioreactor.Another concept,based on continuous agitation of the solid medium,was developed by several teams mentioned below.The bioreactors can be a rotating drum (Fig.3),a per-forated drum (Fig.4)or an horizontal paddle mixer (Fig.5).With or without a water-jacket,this type of reactor is re-quired to be continuously mixed to increase the contact be-tween the reactor wall and the solid medium and also to provide oxygen to the micro-organism.For rotating drum bioreactors,as an horizontal cylinder,the mixing is pro-vided by the tumbling motion of the solid medium which may be aided by baffles on the inner wall of the rotating drum (perforated or not).However,in all these reactors,the mixing is less efficient than with a paddle mixer [9].In-deed,agglomeration of substrate particles during the growth of the mycelium can occur which increases the difficultyofFig.5.Photography of an horizontal paddle mixer used in the Wageningen University of Agriculture.Schematic of a stirred horizontal bioreactor.(1)Air-inlet,(2)temperature probes,(3)water-jacket,(4)paddles,(5)air outlet,(6)agitation motor,(7)reactor,(8)solid medium,(9)agitation shaft.regulating the temperature of the solid medium.Moreover,the oxygen transfer inside these balls of medium,agglomer-ated by the fungal hyphae and also very often by the stick-iness of the substrate used,may be very low or nil.In ad-dition,from an engineering point of view,a water-jacket on a moving body of a reactor causes problems that increase with scale [10].A continuous mixing horizontal paddle mixer (Fig.5)was developed by a Dutch team at Wageningen University.This aseptic fermenter was used for different purposes and to improve simultaneous control of temperature and moisture content.Although heat transport to the bioreactor wall was improved,this device becomes inefficient for larger volume [11]because heat removal only through the wall becomes increasingly inefficient as the volume increases.Generally,a continuous agitation,even if it is gentle,can modify the structure of the solid medium to a pasty texture.Depending upon the nature of the particles (clay granules as support for example),this agitation can also be abrasive and so be harmful for the mycelium especially if the hyphae have no septa.For processes in which the substrate bed must remain static,a reactor designed by ORSTOM team in France and named Zymotis is an interesting equipment [12,13].It con-sists of vertical internal heat transfer plates in which cold water circulates (Fig.6).Between each plate the previously inoculated solid medium is loaded.Thermostated air is in-troduced through the bottom of each partition.This reactor,which looks like a tray reactor where the layers of substrate would be set vertically,appears difficult to work in aseptic conditions.Very often in SSF a shrinkage of the volume of medium occurs during the mycelium growth.With this type of device,A.Durand /Biochemical Engineering Journal 13(2003)113–125117Fig.6.Photography of the Zymotis showing heat exchanger plates for the thermostated water circulation (at left)and during a culture (at right).the risk is that the contacts with the vertical plates will de-crease as the fermentation progresses,which would lead to poor heat transfer and air channelling.Finally,the scale-up of such a design appears very difficult.2.2.Pilot and industrial-scale bioreactorsAs mentioned before,the number of reactor types used at pilot scale and in industry is less wide due,at once to some important reasons and necessities which arethat:Fig.7.Koji-type reactor:(1)Koji room,(2)water valve,(3)UV tube,(4,8,13)air blowers,(5,11)air filters,(6)air outlet,(7)humidifier,(9)heater,(10)air recirculation,(12)air-inlet,(14)trays,(15)tray holders.•above some critical quantity of substrate,the heat removal becomes difficult to solve and restricts the design strate-gies available.The solid medium becomes compacted or creates air channelling,shrinkage,etc.All these factors affect heat and mass transfer,•the properties of the micro-organism with respect to its resistance to mechanical stirring,its oxygen requirement and temperature range.When the mycelium hyphae do not have septa,they can be destroyed by a mechanical stirring.So,the culture layer will be thin to allow heat118 A.Durand/Biochemical Engineering Journal13(2003)113–125removal which automatically orientates to a category of reactor,•the nature of the substrate and the need to pretreat or not it,appropriate procedures for the inoculation,the sterility or the level of contamination acceptable for the process and the application,•the economy of the country where the process is devel-oped especially with respects to the labour cost.Indeed some technologies need more manpower than others,•handling poses different problems such as the ease of filling,emptying and cleaning the reactor.The heat and mass transfer problems identified above can be attributed to poor aeration.This problem can be addressed using the following strategies:(i)the air circulates around the substrate layer or(ii)it goes through it.Within the sec-ond strategy,three possibilities are available:unmixed,in-termittently or continuously mixed beds.2.2.1.SSF bioreactors without forced aerationThis category is ancient and the simplest.Probably differ-ent ancient civilisations have used this technology domesti-cally for fermenting miscellaneous raw agricultural products in baskets.The microbial starter culture might be transferred in the form of a“mouldy medium”.Although this technology has advanced,it is still based on the same principle.Applied on commercial scale,it corresponds to the tray fermenters (Fig.7)as typified by the famous Koji process[14–18].Made of wood,metal or plastic,perforated or not,these trays,con-taining the solid medium at a maximum depth of15cm,are placed in thermostated rooms.The trays are stacked in tiers, one above the other with a gap of a few centimetre.This technology can be scaled-up easily because only the num-ber of trays is increased.Although it has been extensively used in industry(mainly in Asian countries),this technol-ogy requires large areas(incubation rooms)and is labour intensive.It is difficult to apply this technology to sterile processes except if sterile rooms are built and if procedures and equipment for the employees are provided,which will be prohibitive.An alternative could be to use polypropylene semi permeable sterilizable bags to maintain sterility.More-over,some bags have a microporous zone which allows a passive airflow rate from20to2000cm3/(cm2/min).2.2.2.Unmixed SSF bioreactors with forced aerationThe basic design feature of packed-bed bioreactors is the introduction of air through a sieve which supports the sub-strate.In this way,a bioreactor was developed at pre-pilot scale(Fig.8)for defining the control strategy and optimis-ing the air-inlet temperature,the airflow rate,the addition of water and agitation during a SSF process[8].Located in a clean room,the reactor can be pasteurised in situ by steam generated by the water-bath used for the air humidi-fication.This reactor is very simple and can process a few kilograms of dry solid medium.These reactors constitute an interesting tool that can be used in two ways:(i)toanalyse Fig.8.General view and schematic of the unmixed bioreactors with forced aeration.(1)Basket conateining the solid medium,(2)valves for airflow adjustment,(3)air temperature probe,(4)relative humidity probe, (5)draincocks,(6)heating box,(7)humidifier,(8)coil for circulation of cold water,(9)resistive heater.empirically the global evolution of a process and determine the environmental parameters for regulating the temperature and the moisture of the solid medium,(ii)to study mass and heat transfer phenomena and oxygen diffusion[19].Both the reactor diameter and the height of the substrate layer are around40cm,so the quantity of solid medium is suffi-cient to predict what can happen in a larger volume[20].In the absence of mathematical models for the scale-up,these reactors are very useful.No mechanical agitation exists in-side these reactors,but the medium can be manually agi-tated in situ or it can be transferred into a kneading machine and reloaded into the basket.However,this type of device without agitation is limited by the metabolic heat produc-tion.Temperature gradients from the bottom to the top ofA.Durand /Biochemical Engineering Journal 13(2003)113–125119the layer appear unavoidable.As the majority of the heat is eliminated by convection and water evaporation [21],the bed dries out and the water additions needed have to be cal-culated and agitation is required in order to distribute the added water uniformly.To reduce the need for a strong aeration,another concept was recently developed.It consists of the introduction of heat exchangers directly beneath the perforated plates which support the substrate and/or inside the substrate layers.A similar strategy on a lab-scale but with vertical heat exchang-ers has been demonstrated for the Zymotis bioreactor [12].Based on this principle,a first bioreactor was patented [22]and used by a German company (Prophyta)for producing biopesticides in sterile conditions.The fermenter is a tower with perforated plates on which the solid medium is located.Sterile air can go through each plate.Beneath each plate,heat exchangers are located to remove heat during the cultivation (Fig.9).A similar bioreactor,Plafractor TM ,was patented by an Indian company,Biocon,[23].Metabolic heat,as in the previous reactor,is mainly removed by conduction.This reactor was constructed by stacking and interconnecting in-dividual modules (Fig.10).Non-communicatingchannelsFig.9.Schematic of the patented industrial bioreactor showing the exchanger plates under each tray [22].deliver cooling and heating fluids sandwiched between two municating channels can deliver fluids for ster-ilising (with steam or ethylene oxide for example),for ad-justing the moisture and oxygen content and for extracting the compound of interest after the cultivation.Moreover,the interior of each module has a mixing arm that revolves about the central axis of the module while rotating.This reactor has been used mostly for metabolite production.In the patent,a maximum quantity of 20kg of wheat bran was mentioned with approximately 22,600cm 2plate area,but the number of modules was not mentioned.Finally,no de-tails were given about the disposal of the waste product,the cleaning procedure which seems relatively complicated and generally the possibility to scale-up this device.2.2.3.Continuously mixed SSF bioreactors with air circulationThis category is essentially a rotating drum because con-tinuous mixing is necessary to maximize the exposure of each substrate particle to the thermostated air circulating in the headspace.Different teams have worked on this design and it is mostly used at lab and pre-pilot scale.Although120 A.Durand /Biochemical Engineering Journal 13(2003)113–125Fig.10.Scheamtic of the Plafractor TM reactor [23].rotating drums have been described in the past,the largest reactor recently cited in the literature was a 200l stainless steel rotating drum (Ø56cm and 90cm long)which used 10kg of steamed wheat bran as substrate [24]for kinetic studies of Rhizopus .Researches were carried out at lab-scale to study the efficiency of this design,the role of the baffles and the influence of the filling (amount of substrate per unit volume)on the mass transfer by using tracer or image analysis [25–27].These works introduced the rational design and scale-up of this type of reactor.In several cases,the mycelium and the substrate particles,particularly starchy and sticky materials,agglomerate.Under these conditions,even with baffles inside the drum,it was very difficult to separate these aggregates,consequently,the heat,mass and oxygen transfers were greatly reduced.When the rotation rate of the drum is increased,it can affect the mycelium growth presumably because of shear effects [25].For a discontinuously rotating drum,the design is iden-tical to the reactor described above but between two agi-tations,it operates like a tray reactor.So,it is absolutely necessary to limit the height of the substrate layer,other-wise it will be necessary to continuously agitate due to the heat accumulation and,taking into account the poor ther-mal conductivity of the air,the medium temperature will in-evitably increase.Very few studies have been published on this ing this rotating drum,a strategy for regulating the medium temperature was described in a thesis [28]and in a publication [29].It consists of activating the rotation of the drum in response to the temperature measured by a thermocouple in the medium.Efficient for a 4.7l workingA.Durand /Biochemical Engineering Journal 13(2003)113–125121Fig.11.Discontinuously rotating drum [28].volume (Fig.11),on soy beans with Rhizopus ,for tempe production,no scale-up studies have been attempted.2.2.4.Intermittently mixed bed bioreactors with forced aerationIn general,these bioreactors can be described as packed beds in which conditioned air passes through the bed.An agitation device is periodically used to mix the bed and at the same time,water is sprayed if necessary.The design of these reactors,the capacity of which varies from afew Fig.12.Photography and schematic of the Koji making equipment:(1)Koji room,(2)rotating perforated table,(3)turning machine,(4,11)screw and machine for unloading,(5)air conditioner,(6)fan,(7)air outlet,(S)dampers (9)air filter,(10)machine for filling,(12)control board.kilograms to several tons,is influenced the necessity or not to operate in sterile conditions.For non-sterile processes ,a number of advances have been done in the design and application of such bioreactors.One design is represented by the rotary type automatic Koji making equipment marketed by Fujiwara in Japan (Fig.12).The treated substrate is heaped up on a rotary disc.De-pending on the diameter of this disc,different working volumes are available but always with a layer of maximum thickness 50cm.This non-sterile reactor operates with a122 A.Durand /Biochemical Engineering Journal 13(2003)113–125microcomputer which controls all the parameters (tempera-ture of the air-inlet,air flow rate and agitation periods).The main drawback of this equipment is the need to prepare and inoculate the substrate in other equipment before filling the reactor.Nevertheless this type of design is widely used in Asian countries.Similar to the reactors used in the barley malting process,huge equipment has been built for the first step of the process for making soy sauce.A specific building contains the solid state reactor which is generally rectangular with a length of several meters.Several tons of pretreated and inoculated substrate are put on a wire mesh and conditioned air is forced through the layer.An agitator trolley periodically mixes the solid medium.Although this kind of reactor is very simple and basic,it is widely used in many Asian manufacturers of soy sauces.An INRA team in Dijon (France)has developed a non-sterile process strategy based on the following principle (Fig.13).The temperature (T m )and the moisture (W A m )of medium are maintained by a regulation of the temperature,relative humidity and flow rate of the air input.It is also nec-essary to spray water (E)and agitate (A)periodically.TheFig.14.Pilot plant reactor [30]:Photography showing a general view of the reactor (left),a detail of the swelling joints.A schematic diagram of this pilot plant.(1)Carriage motor,(2)screw motor,(3)valves for inoculum and water spraying,(4)temperature probes,(5)weight gauges,(6)relative humidity probe,(7)cooler,(8)humidifier by steam injection,(9)airflow meter,(10)fan,(11)heater,(12)air filter,(13)cooler.Fig.13.General schematic of the intermittently packed bed reactor with forced aeration.(T in ,HR in and D in )respectively the temperature,relative humidity and flow rate of the air-inlet,(T out ,HR out and D out ),respectively,the temperature,relative humidity and flow rate of the air outlet,(T m )temperature of the solid medium,(WA m )water amount of the solid medium,(M g )total mass of the solid medium,(A)agitation,(E)water spray.A.Durand /Biochemical Engineering Journal 13(2003)113–125123volume of water sprayed is calculated from on line measure-ments of the total mass of the medium (M g )and by estimat-ing the mass losses due to respiration (CO 2).On this basis,a reactor of 1.6m 3capacity using 1t of sugar beet pulp (with 25%of dry matter)per batch was reported [20].This reactor has been successfully used for different applications includ-ing protein enrichment of agro-industrial by-products,pro-duction of enzymes or biopesticides [30].The system has been since continuously pared to the first re-actor,the main changes (Fig.14)were in the equipment it-self with some accessories (pump for inoculation and water spraying),the air conditioning and the software for the con-trol and the regulation of the parameters during the process.Particularly,a mathematical model has been established for maintaining the moisture of the medium during the process by taking into account the dry matter losses and the evapora-tion due to the aeration.Moreover,this reactor is closed by a cover in three parts allowing the passage of the screw axis during the mixing.By this way,it is possible to pasteurise the reactor and/or to treat the substrate in situ,near 80◦ing the same design,two larger reactors (each with overall dimensions of 17.6m ×3.6m ×2.0m)and a maxi-mum working capacity of 50t (20%dry matter)were con-structed [31]to demonstrate the potential industrial-scale-up of this fermenter.For sterile processes ,the reactors based on this same prin-ciple are smaller and,currently,no industrial application has been published in the literature.Such sterile processes are necessarybecause:Fig.16.Photography and schematic diagram of the sterile reactor developed by the National Institute of Agronomic Research in Dijon [30].(F)Air filter,(HC)humidification chamber,(HB)heating battery,(BP)by-pass,(CB)cooling battery,(HM)probe for air relative humidity measurement,(TP)probe for medium temperature measurement,(WG)weight gauges,(SH)sterile sample handling,(JR)water temperature regulation in the double jacket,(AD)planetary agitation device,(M)motor for agitation,(IS)sterile system for adding inoculum and solutions,(CO)water aircondenser.Fig.15.Photography of the ribbon mixer developed by Wageningen University of Agriculture [32].124 A.Durand/Biochemical Engineering Journal13(2003)113–125•the product obtained must be sterile for application and legislative reasons(food and pharmaceutical industries for example),•the micro-organism used has a very slow growth rate and so must be cultivated in clean conditions.Indeed,usually, it is considered that beyond3days cultivation,it is very difficult to work in non-sterile conditions.An original design has been developed by the Wa-geningen University in Holland and used at pilot scale for studying production of a biopesticide[32].This reactor with a total capacity of50l can hold up to20kg of wet cereal grains substrate.It consists of a conical vessel mixed by a ribbon at the wall(Fig.15).This reactor,developed in co-operation with Hosokawa Micron,is sterilisable in situ by steam.Sensors register the temperature at several heights in the bed,also during mixing.Another bioreactor with a50l bed was patented by Du-rand et al.[33].This reactor,which has a planetary mixing device(Fig.16)is entirely piloted by a micro-computer dur-ing the different process steps:sterilisation of the bioreac-tor while empty,sterilisation of the medium,process control during the fermentation and data acquisition.Among oth-ers,this reactor was used for the production by fed-batch SSF of gibberellic acid(Bandelier et al.,1997)and for the production(after15days cultivation)of conidia for biolog-ical control application[34].Up to date,no scale-up of this device was carried out in the industry.3.Conclusions and perspectivesOver the last10years,significant progress has been made in the design of solid state reactors.More and more,studies appear in the literature with promising perspectives.Some designs,such as the rocking drum bioreactor,appear more difficult to scale-up than others[13].When we analyse the evolution of the solid state processes in the world,we ob-serve that it is not a matter of chance that the research and the industrial applications are most important in the Asian countries.An ancient and important tradition,mainly for the food industries,promoted this evolution.But,despite this success,little improvements were carried out from the tradi-tional Koji equipment and,in most cases,the scaling-up has only consisted in mechanising the tray fermenter.It can also be observed that if a pilot reactor exists,empirical studies can be conducted for effective process control design and successful industrial-scale-up[2].Up to now,the majority of the scale-up was done using the rules of thumb,but taking into account the great advan-tages of the SSF process,several research teams are work-ing around the world and significant advances have been made in the development of quantitative approaches for heat and mass transfer([35,36];Ashley et al.,1999),mathe-matical modelling[13],measurement of some process vari-ables[37,38]and for the development of growth models[6].Interesting approaches have been used by several workers not only to characterise the oxygen transfer and the effects of air pressure oscillation amplitude[39],but also to attempt to better understand the behaviour of the micro-organism in such solid state systems[40].However,some aspects of SSF processes still need re-search:development of probes mainly for moisture measure-ment,control and regulation of process variables,analytical procedures well adapted to these specific media,measure-ment of the gaseous environment.Finally,and especially if the aim of the studies is not only academic but for industrial applications,it is important to keep in mind that some phe-nomenon studied at laboratory-scale are not representative of large-scale because the scaling-up is impossible.Very of-ten,the problems linked to the increase in the volume(mass compaction,shrinkage,diminution of the heat transfer,etc.) do not appear at the bench scale and serious errors can be made in the choice of bioreactor design or process control strategy.If an industrial submerged fermentation process is run-ning,it would be unrealistic to imagine its replacement by a SSF process taking into account the level of investment already done by the industry[1].Despite a volumetric pro-ductivity,very often greatly higher obtained in SSF(around 10times more for enzyme production for example),it is difficult on an economical point of view to change the pro-duction tool.But by improving the reactor and the process control;the industry could consider the solid state fermen-tation as a very attractive alternative when new investments are decided or when new processes are developed.Finally, for some industrial applications(production of spores for cheese making for example),SSF constitutes the sole so-lution for a production process and now,more viable and optimised tool can be proposed to the industry. 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