Chlorine-free extraction of cellulose from rice husk and whisker isolation
- 格式:pdf
- 大小:899.21 KB
- 文档页数:8
小球藻提取物对 CCl4 所致小鼠急性肝损伤的作用讨论本文从网络收集而来,上传到平台为了帮到更多的人,如果您需要使用本文档,请点击下载按钮下载本文档(有偿下载),另外祝您生活愉快,工作顺利,万事如意!肝脏是机体重要的代谢器官,是化学毒物或药物在体内代谢或转化的重要场所,因此肝脏极易受到外源性物质的攻击,从而引发急性或慢性损伤。
目前,肝病已成为我国最突出的公共卫生问题之一,是与艾滋病、肺结核和血吸虫病并列危害最严重的四大传染疾病之一。
因而,研究抗肝脏疾病的有效功能性食品成分或药物显得犹为重要。
小球藻(Chlorella vulgaris)是一类普生性球形单细胞绿藻,生态分布极广,在淡水、海水中均有发现。
小球藻含有丰富的蛋白质、多糖、脂质、叶绿素、维生素、微量元素、核酸和一些生物活性代谢产物,有“药物藻类”之美誉。
研究表明,小球藻具有激活淋巴细胞、增强免疫力、抵抗外来疾病的入侵、促进人体受伤组织修复等功效,降血压、降血脂、抗氧化、抗肿瘤、解毒等功效。
四氯化碳(CC14)是一种常见的肝毒性化合物,可诱导急性肝损伤、肝纤维化、肝硬化和肝癌等肝脏疾病的发生,常用于实验室急性肝损伤的造模。
本实验通过CC14 致小鼠肝损伤模型,探讨小球藻水提物对小鼠急性肝损伤的保护作用与机制,以期为小球藻功能性食品的开发及应用提供实验依据。
1 材料与方法材料四氯化碳(CCl4),Sigma;玉米油;丙氨酸氨基转移酶(ALT)试剂盒,Biochem;天冬氨酸氨基转移酶(AST)试剂盒,Biochem;Bio-Plex Multiplex 细胞因子试剂盒,Bio-Rad。
实验动物健康雄性ICR 小鼠60 只,体重(20~25 g)。
小球藻由韩国Marine Microalgae Culture Center 提供。
小球藻水提物的制备将500 g 干燥的小球藻粉混悬于适量蒸馏水中,90 ℃,30 min,提取两次,合并提取液,离心60 min,上清液用1 μm 玻璃纤维滤器过滤后,冷冻干燥,得粗粉63 g,于-20 ℃保存备用。
一种新颖的杀真菌药物绿原酸拟肽的发现Mohsen Daneshtalab加拿大,圣约翰,纽芬兰纪念大学,药学院。
摘要在最近几十年中威胁免疫功能低下患者生命的真菌感染有了极大的增加。
据估计,由医院获得感染的所有死亡的40%由于侵入真菌所造成的感染。
目前的治疗方案或者造成严重毒性,或成为无效的抗真菌菌株药物。
因此,发现和开发新的抗真菌药物在经济上可行,具有良好的治疗价值,并解决毒性和抗菌品种的问题是非常重要的。
我们已最近设计并合成了一系列绿原酸的拟肽以使用结构为基础的方法循环多肽的candin抗真菌类。
这些新颖的完全合成的化合物显示出有可能有抗真菌活性反抗致病性真菌的毒性非常低的对盐水虾。
这种可能存在的新颖的作用机制和经济上的可行性是合成这类化合物有吸引力的特点,使这一类化合物不同于已经利用的抗真菌药物。
导言在最近几十年中免疫功能低下患者威胁生命的真菌感染急剧增加,如接受癌症化疗,器官移植,和艾滋病患者(1-4)。
念珠菌。
脂多糖,如papulacandins ,(包括白色念珠菌和非白色)已侵入的主要病原体(2,5,6)。
曲霉菌(致病病原侵袭肺形成曲霉病)。
死亡率最高的是接受骨髓移植手术的人(7),而感染艾滋病毒的患者对粘膜念珠菌敏感,隐球菌性脑膜炎,散发组织胞浆菌病,球孢子菌病,和间质性浆细胞(8-10)。
对于不配合治疗的患者治疗系统性和侵入性真菌感染是一个重大挑战。
两性霉素B仍然是最佳治疗最严重侵入性真菌感染。
然而,它产生急性和慢性的副作用,这可能降低新配方的脂质体(11),脂质复合物(12),和胶体分散系(13,14)。
唑类抗真菌药物包括氟康唑,伊曲康唑,和最近提出的posaconazole ,完全是人工合成的化合物,广泛的抑菌活性对大多数酵母菌和丝状真菌。
尽管免于严重毒性,他们可能会产生内分泌副作用,如睾丸素和糖皮质激素,造成乳房和肾上腺皮质功能低下(15,16)。
应用唑类另一个重大局限性,特别是氟康唑,是出现了有抵抗力的抗真菌株包括念珠菌。
鱼腥草黄酮的提取及对羟自由基的清除能力
周桃英
【期刊名称】《江苏农业科学》
【年(卷),期】2011(039)006
【摘要】采用超声波辅助法萃取鱼腥草黄酮,并对工艺进行优化,以期获得最佳的提取方法,同时对其抗氧化特性进行了研究.结果表明,鱼腥草黄酮超声波辅助法提取的最佳工艺是液料比45mL:1g,乙醇浓度60%,超声35 min,温度为35℃,此时鱼腥草黄酮提取量为11.91 mg/g.鱼腥草黄酮对羟自由基有一定的清除作用.
【总页数】3页(P529-531)
【作者】周桃英
【作者单位】黄冈职业技术学院生物系,湖北黄冈438002
【正文语种】中文
【中图分类】S567.230.1
【相关文献】
1.不同处理香蕉花黄酮提取工艺及DPPH自由基清除能力研究
2.九种药用植物花黄酮类物质提取及对羟自由基清除能力的研究
3.鱼腥草中黄酮类化合物的提取工艺及其对自由基清除能力的研究
4.响应面优化超声辅助提取黄秋葵嫩果黄酮工艺及其清除羟自由基能力
5.黑豆异黄酮的提取分离及其对DPPH自由基的清除能力
因版权原因,仅展示原文概要,查看原文内容请购买。
UV法建立槲寄生多糖口服液含量测定方法1. 材料与设备1.1 材料槲寄生(采自吉林省永吉县,寄主为杨树)、葡萄糖标准品(2016091067,天津市致远化学试剂有限公司)、蔗糖、亚硫酸氢钠、苯甲酸钠、95%乙醇、三氯乙酸(TCA)、苯酚、浓硫酸。
以上辅料为药用级别,试剂为分析纯,均由吉林农业科技学院实验室提供。
1.2 设备紫外可见分光光度计(UV-5100,上海元析仪器有限公司);数显恒温电热套(HDM.500C,金坛市科析仪器有限公司);中药粉碎机(LG-08A,浙江瑞安市百信药机器械厂);标准筛(浙江上虞市宏兴仪器厂)。
2. 方法与结果2.1 长白山槲寄生多糖的提取称取适量长白山槲寄生粉末在70℃下干燥12h,粉碎,过40目筛,称取过筛后的槲寄生粉末10g,料液比按1∶26,在95℃水温下提取3h,得到槲寄生多糖提取液,用4层纱布过滤去除残渣,将提取液浓缩后,加入95%乙醇后置冰箱冷藏室,次日除去乙醇,沉淀物用纯水将溶解,向其中加入50% TCA,调浓度为10%,离心(4000r/ min)去除沉淀物,得槲寄生脱蛋白多糖水提取液。
2.3.2 苯酚溶液的配置取苯酚放于烧杯中置于60℃水浴中溶解,用蒸馏水定容摇匀,配制成浓度为6%苯酚溶液,于棕色瓶中保存,备用。
2.3.3 标准曲线的绘制如图1所示,精密量取对照品溶液0.1、0.2、0.3、0.4、0.5、0.6、0.7ml,分别加水至2.0 ml,摇匀后精密加入1.0ml 6%苯酚,摇匀后精密加入5.0ml浓硫酸,放冷至室温后,沸水浴显色2.2 长白山槲寄生口服液制备取槲寄生脱蛋白多糖水提取液200ml,定容至1000ml。
取出稀释液100ml,加入蔗糖3mg,亚硫酸氢钠10mg,苯甲酸钠40mg,溶解后灌封,灭菌,得到长白山槲寄生口服液。
2.3 UV法对长白山槲寄生口服液的含量测定2.3.1 对照品溶液的制备精密称定无水葡萄糖对照品10mg,配制成浓度为0.1mg/ml的溶液。
专利名称:一种重组大肠杆菌周质蛋白液的制备方法专利类型:发明专利
发明人:林俊
申请号:CN98122065.7
申请日:19981204
公开号:CN1227873A
公开日:
19990908
专利内容由知识产权出版社提供
摘要:一种重组大肠杆菌周质蛋白液的制备方法,通过使用盐处理大肠杆菌细胞以增加细胞外膜的通透性,从而达到专一抽提细胞周质中的蛋白之目的。
本方法有效地防止了制备细胞周质液时对细胞细胞壁和内膜的损害,从而减少了细胞内干扰物质对目的蛋白分离纯化的影响。
它将促进周质分泌型工程菌的应用,特别是为该类型的基因工程菌工业化应用开辟道路。
申请人:中国科学院上海细胞生物学研究所
地址:200031 上海市岳阳路320号
国籍:CN
代理机构:上海华东专利事务所
代理人:费开逵
更多信息请下载全文后查看。
纸业专业英语词汇翻译(C3)cellu-sizer 压力式纤维筛分器celsius scale 摄氏(温度)表,摄氏温标celsius thermometer 摄氏温度计cembra fir (pinus cembra, pinus sibirica) 石松,西伯利亚红松cement bonded pulpstone 水泥磨石cement-quartz mortar 水泥石英砂浆cemented steel 渗碳钢cementing substance 粘合剂center ply 芯层;中间层center rewind 轴式卷取复卷法center stock 芯层浆料center winding 轴式卷取centigrade scale 摄氏(温度)表,摄氏温标centigrade thermometer 摄氏温度计centipoise 厘泊central board 中央控制板central layer of secondary 次生壁中层central processor 中央(信息)处理机central ray 中间细胞射线centralized instrument panel 仪表中央控制盘centricleaner 锥形除渣器centriclone 锥形除渣器centriffler 两段除渣器centrifiner 立式除渣器centrifugal 离心式centrifugal blower 离心式鼓风机centrifugal classifier 离心分选机centrifugal cleaner 锥形除渣器,离心净浆器centrifugal exhauster 离心式抽风机centrifugal fan 离心式风机centrifugal filtration 离心过滤centrifugal force 离心力centrifugal pump 离心泵centrifugal sereen 离心式筛浆机,(离心式)圆筛centrifugal scrubber 离心除尘器centrifugal vacuum compressor 离心式真空压缩机centrifugation 离惦(分离)centrifuge 离心机centri-petal 中心瓣centripress drainer 离心压榨脱水机centri-sorter 旋翼筛ceramic coating 瓷釉涂布ceramic fiber 陶瓷纤维ceramic grindstone 烧结磨石ceramic suction box cover 真空箱陶瓷面板ceramic time 瓷砖ceramics 陶瓷(制品)cercal straw 谷草ceresine wax (纯)地蜡cerex 聚酰胺合成纸(美国monsanto产品,商业名称)chaff cutter 切草机chain 链;链条;(悬竿式干燥室用)送棒链chain barker 链式剥皮机chain conveyer 链式运输机chain drive 链传动chain flail barker 链式剥皮机chain grate 链栅式炉篦chain grate stoker 链栅式给煤器chain grinder 链式磨木机chain length 链长chain molecule 链分子chain marks (纸张)线痕(纸病)chain peeler 链式剥皮机chain reaction 连锁反应chain saw 链锯chainlide cell 链状细胞chalk 白垩chalking 白垩处理;粉化chalking appearance 粉状;白垩化纸面chamber dryer 干燥室chamotte 耐火粘土chamotte brick 粘土耐火砖change of deckle 更换定边带changeover switch 转换开关changing of wire 换网changing valve 转换阀chapman smoothness tester chapman平滑度测定仪char 炭;烧焦characteristic curve 特性曲线characteristic test 特性测定,特性试验characteristics 特性charcoal 木炭charge 装,装料;充电;电荷charger 加料器;装锅器charging door 装料楼面charging floor 装料楼面charging hole 装料日charging hopper 装料斗charging of acid 送(料)液charging of chips 装料,装木片charging of liquor 送液chart 图表chattering of rolls 辊筒跳动check 核对,校核;抑制,抑止check damper 风挡check plate 挡板check valve 单向阀,止逆阀checking 核对;检查cheese roll 弧形辊,弓形辊,舒展辊cheese wrapper 奶酪包装纸chelate 螯合剂chelating 螯合作用chemical affinity 化学亲合势,化学亲合能chemical agent 化学药剂chemical barking 化学剥皮chemical bond 化学键chemical composition 化学成分chemical consumption 化学药品消耗量chemical debarking 化学剥皮法chemical degradation 化学降解chemical efficiency 化学(反应)效率chemical filter 化学滤毒器chemical makeup 补充药品chemical oxygen demand 化学需氧量chemical recovery 化学药品回收,碱回收chemical resistance 化学阻力chemical screenings 化学浆筛渣chemical structure 化学结构chemical test 化学试验chemical-to-wood ratio 化学药剂与木材的比值chemical treatment 化学处理chemical wood(pulp) 化学木浆chemically stable 化学稳定性chemi-finer 高浓单动盘磨机chemi groundwood 化学机械木浆chemipulp hot acid system 热酸回收系统chemipulp system 热酸回收系统chemipulper 管式连续蒸煮器chemism 化学机理chemisorption 化学吸着chefry(prunus) 樱属;李属chefry birch (betula lenta l.) 矮桦,樱皮桦树chest 槽,池,箱chestnut tree 栗树cheviot 拟花岗岩纸chief chemist 总化学师chief constituents 主要组分chief engineer 总工程师chili wrapper 辣椒包装纸chilled iron roll 冷铸铁辊chill(ed) roll 冷铸辊chime rings 凸出圆环chimney 烟囱china grass(boehmeria nivea) 麻chinese arbor-vitae (biota orientalis endz.) 侧柏chinese red pine(pinus massoniana lamb.) 马尾松chip 木片,切片chip assorting machine 木片筛chip belt feeder 木片皮带给料器chip bin 木片仓;竹片仓chip charger 木片装料器chip charging with packer 机械装锅chip charging without packer 自然装锅chip chute 木片斜槽chip classification 木片筛分chip classifier 木片筛分器chip compression debarking press 双辊木片剥皮机chip conveyer 木片输送机chip crusher 木片再碎机chip dimensions 木片规格chip distributor 木片装锅器chip dust 木屑,木片碎屑chip duster 切片除尘机chip elevator 木片提升机chip feeder 木片喂料器chip filler 木片装锅器chip filling 木片装锅chip filling device 木片装锅器chip filling without filler (木片)自然装锅chip fractionater 木片筛分器chip grinder 木片磨浆机chip groundwood 木片磨木浆chip hopper 装锅漏漏斗chip mechanical pulp 木片磨森乐,木片机械浆chip meter 木片装锅计量器chip packer 木片装锅器chip packing device 木片装锅器chip pile 木片堆chip recrusher 木片再碎机chip screen 木片筛;竹片筛chip silo 木片仓;竹片仓chip stock 粗浆chip yard 木片贮存场,贮木场chipper 削片机chipper disc (削片机)刀盘chipper disk (削片机)刀盘chipper knife 削片刀chipper spout (削片机)喂料口chipperman 削片工chipping 削片chisel edge 刀口,刀刃chlorate 氯酸盐chlor-fastness 氯牢固性chloric acid 氯酸chloride 氯化物chlorinated lignin 氯化木素chlorinated lime 漂白粉chlorinated starch 氯化淀粉chlorinated stock washer 氯化段洗浆机chlorinating agent 氯化剂chlorination 氯化(作用)chlorination stage 氯化阶段chlorination tank 氯化槽chlorination tower 氯化塔chlorination unit 氯化装置chlorinator 氯化器chlorinator with injector 喷射(式)氯化器chlorinator with spiral tubing 内螺旋管氯化器chlorine 氯,氯气chlorine cell 制氯电解池chlorine compound 氯化物chlorine consumption 氯耗,耗氧量chlorine cylinder 液氯瓶chlorine dioxide 二氧化氯chlorine dioxide bleaching 二氧化氯漂白chlorine dioxide tower 二氧化氯处理塔chlorine dissolving tank 溶氯槽chlorine gas 氯气chlorine monoxide 一氧化氯chlorine number 氯价chlorine requirement 需氯量chlorine resistant 抗氯性chlorine still 氯气发生器chlorine storage tank 氯气贮槽chlorine water 氯水chlorite 亚氯酸盐chlorite bleaching 亚氯酸盐漂白chlorcacetic acid 氯醋酸chlorolignin 氯化木素chlorohydrin lignin 氯醇木素chloromix tower 顶氯化塔chlorophyll 叶绿素chlorous acid 亚氯酸choke valve 阻气阀chopped reed 苇片chopped straw 草片chopper 切断装置chopping 切断chromate 铬酸盐chromaticity 色渡chromaticity diagram 色度图chromato gram 色谱chromatographic analysis 色谱分析,色层分析chromatographic technique 色层分析,色谱分析chrome brick 铬砖chrome nickle steel 镍铬钢chrome steel 铬钢chrome vanadium steel 铬钒钢chrome wire 铬网chrome yellow 铬黄chromium oxide 氧化铬chromometer 比色汁chromophore 发色团chromophoric group 发色基团chuck 夹盘,夹头churn 乳化器;搅拌器chute 斜槽;送料槽cigarette tissue machine 卷烟纸机cigarette wrapping 卷烟包装纸cinchona(cinchona) 金鸡钠树属cinder 矿渣;炉渣cinder dust 炉灰cinnamic aldehyde 肉桂醛cipher 密码;(纸张)水印circuit 电路;回路;线路circuit break 断路circuit bresker 断电器;电开关;断路器circuit diagram 电路图;线路(图)circular chart 圆形(表盘)记录纸circular cutter 圆盘切料机circular former 双曲网成形装置circular saw 圆锯circular slitting knife 盘刀;复卷机固定刀circular swing saw 摆动圆锯circulating air 循环空气;循环热风circulating pump 循环泵circulating stock chamber 溢流箱circulating system 循环系统circulating water 循环水circumferential speed 圆周速度cistern 槽clack valve 瓣阀,逆止阀clack digester 复合钢板蒸煮锅clack metal 复合金属板cladding 复合,复盖claflin refiner 大锥度精磨机clamp 夹;夹板,压板;钳clamp mark 夹痕clamp truck 带夹器的小车clamping length 夹具的距离clamping rings 固定圆环clapped valve 逆止阀clarification 澄清clarified liquer 澄清液clarifier 澄清器clarify 澄清clasp machine 订书机classification 筛分(作用),分选(作用);分类classifier 分离器;澄清器;筛分器classify 筛分,分选;分类;区分claw 爪子claw wrench 爪型板钳。
高效液相色谱法测定叶下珠中槲皮素的含量高效液相色谱法(High Performance Liquid Chromatography, HPLC)是一种广泛应用于化学、食品、医药等领域的分析方法。
它以溶液作为流动相,通过与固定在柱上的固定相相互作用,实现化合物的分离和定量分析。
叶下珠是一种常用的中药材,其主要成分之一为槲皮素。
槲皮素是一种黄酮类化合物,具有抗氧化、抗炎、抗癌等多种生物活性,因此对于叶下珠中槲皮素的含量分析是一项重要的研究工作。
高效液相色谱法测定叶下珠中槲皮素的含量的步骤如下:样品的制备:首先将叶下珠样品粉碎成粉末,然后取适量样品称重,加入适量的提取剂使其浸泡,同时进行超声提取或加热提取。
提取剂的选择可以根据所需的分析指标进行选择,一般常用的提取剂包括乙腈、甲醇等。
提取时间和温度可以进行优化,以获取更好的提取效果。
样品的过滤:将提取后的样品用滤纸或微孔过滤膜过滤,去除其中的杂质和大颗粒物质,得到清澈的提取溶液。
色谱柱的选择:选择适当的色谱柱对槲皮素进行分离和定量分析。
常用的色谱柱包括C18柱、C8柱、C4柱等,根据槲皮素的性质选择相应的色谱柱。
流动相的选择:根据槲皮素的极性特点选择合适的流动相。
一般流动相可以是水和有机溶剂(如甲醇、乙腈)的混合物,其中有机溶剂的比例可以根据所需的分离效果进行调整。
色谱条件的设定:根据分析的需要,设定合适的色谱条件,包括流速、梯度洗脱条件、检测波长等。
标准曲线的制备:通过配制不同浓度的槲皮素标准溶液,利用色谱法进行分析测定,并绘制标准曲线。
一般情况下,标准曲线的线性范围为0.1-100 μg/mL。
样品的测定:将样品溶液注入色谱系统,经过一定的时间后,所得的色谱图上会出现峰,峰的面积与槲皮素的浓度是成正比的,通过标准曲线可以计算出样品中槲皮素的含量。
结果的计算与分析:根据样品的峰面积值和标准曲线,可以计算出样品中槲皮素的含量,并进行统计分析。
使用高效液相色谱法测定叶下珠中槲皮素的含量有许多优点,首先是分离效果好,可以对复杂的样品进行分析;其次是灵敏度高,可以对低浓度的槲皮素进行准确测定;此外,该方法还具有操作简便、分析时间短等优点。
专利名称:一种芦荟双氢香豆素及分离方法和应用专利类型:发明专利
发明人:刘扬,王红梅,张秀凤,田秋
申请号:CN200410070996.X
申请日:20040806
公开号:CN1730479A
公开日:
20060208
专利内容由知识产权出版社提供
摘要:一种芦荟双氢香豆素及分离和应用,其分离方法包括将中药芦荟浸膏以酸性氯仿进行抽提,将提取液浓缩后以乙醇水溶液溶解,然后依次以正己烷、氯仿、醇水进行溶剂分配。
对氯仿部分浓缩后进行柱层析,多次洗脱后,得到一纯净化合物。
药理实验证实它具有抗氧化性,免疫调节作用和抗肿瘤活性。
整个提取工艺过程简单,成本低。
该提取物具有较大的应用价值。
申请人:中国科学院化学研究所
地址:100080 北京市海淀区中关村北一街2号
国籍:CN
代理机构:中科专利商标代理有限责任公司
代理人:周长兴
更多信息请下载全文后查看。
专利名称:一种红花注射液中游离槲皮素的富集方法及含量测定方法
专利类型:发明专利
发明人:严敏嘉,董礼,胡莹莹,史琳莉
申请号:CN201911320843.9
申请日:20191219
公开号:CN110967426A
公开日:
20200407
专利内容由知识产权出版社提供
摘要:本发明提供一种红花注射液中游离槲皮素的富集方法及含量测定方法。
所述红花注射液中游离槲皮素的富集方法采用盐析吸附法,加过量盐使红花注射液中的游离槲皮素析出并溶于乙腈,通过乙腈反复充分吸附即可实现红花注射液中的游离槲皮素的富集。
该方法中使用乙腈富集的游离槲皮素纯度高,杂质含量较低,降低了在后续游离槲皮素含量测定过程中杂质的干扰,提高了检测准确度。
所述红花注射液中游离槲皮素的含量测定方法精密度高,重复性好,稳定性好,准确度高。
申请人:华润三九(雅安)药业有限公司
地址:625000 四川省雅安市雨城区南坝中街1号
国籍:CN
代理机构:北京超凡宏宇专利代理事务所(特殊普通合伙)
代理人:李双艳
更多信息请下载全文后查看。
紫茎泽兰提取物国内研究进展作者:董欣悦王见来源:《绿色科技》2013年第12期摘要:概述了紫茎泽兰的基本特征、起源和在我国分布的情况。
综述了紫茎泽兰的研究现状,主要包括:从遗传特性上探讨了紫茎泽兰的生长优势;分析了紫茎泽兰的化学成分;研究了紫茎泽兰提取液的提取方式;根据紫茎泽兰提取液的化学性质做了杀虫活性的研究;最后指出了目前我国紫茎泽兰的开发利用存在的问题,并对我国对紫茎泽兰提取液的开发和合理利用提出了相关的建议。
关键词:紫茎泽兰;遗传性;化学成分;提取液;杀虫活性中图分类号:S451文献标识码:B文章编号:16749944(2013)120063031引言紫茎泽兰(Eupatorium adenophorum)作为外来入侵物种广泛分布于云南省各地,并已成为一种恶性杂草,近些年来在贵州、四川等地有蔓延发展的趋势,给这些地区的农牧业生产带来了严重的影响。
本文试图从天然杀虫剂的角度出发,研究紫茎泽兰精油杀虫活性,为有效地开发丰富的紫茎泽兰资源,使之变害为利提供参考。
2紫茎泽兰种质资源概述紫茎泽兰是菊科泽兰属的一种有毒植物,俗称“败马草”、“黑茎草”、“臭草”、“飞机草”、“霸王草”等,为多年生粗壮草本,呈半灌木状,高0.8~1.2m最高可达3.26m,紫茎泽兰根系发达,茎直立茎杆圆实心,茎和叶柄紫色故名紫茎泽兰,叶片菱形对生,三出脉,深绿色,叶缘前半部有粗锯齿,花白色,头状伞房花序,每年1~2月现蕾,2~3月开花,3~4月种子成熟。
紫茎泽兰种子很小,瘦果顶端有冠毛,种子千粒质量0.040~0.045g,成熟的种子可随风四处飘扬,1株植物可产数10万粒种子,传播速度快,侵占能力强,是一种世界性的有害有毒植物。
紫茎泽兰是我国外来入侵物种中危害最为严重的植物之一,原产于中美洲的墨西哥和哥斯达黎加。
作为一种有害的外来物种现已在夏威夷、澳大利亚、新西兰、泰国等地爆发式繁衍,广泛分布在世界热带、亚热带30多个国家和地区。
Carbohydrate Polymers 87 (2012) 1131–1138Contents lists available at SciVerse ScienceDirectCarbohydratePolymersj o u r n a l h o m e p a g e :w w w.e l s e v i e r.c o m /l o c a t e /c a r b p olChlorine-free extraction of cellulose from rice husk and whisker isolationSimone M.L.Rosa,Noor Rehman,Maria Inez G.de Miranda,Sônia M.B.Nachtigall,Clara I.D.Bica ∗Chemistry Institute,Federal University of Rio Grande do Sul,PO Box 15003,ZIP 91501-970,Porto Alegre,RS,Brazila r t i c l ei n f oArticle history:Received 13May 2011Received in revised form 1August 2011Accepted 24August 2011Available online 31 August 2011Keywords:Cellulose whiskers Rice husk Biomaterials MicroscopyPeroxide bleaching Thermal analysisa b s t r a c tThis work reports the isolation of cellulose whiskers from rice husk (RH)by means of an environ-mental friendly process for cellulose extraction and bleaching.The multistep process begins with the removal of pectin,cutin,waxes and other extractives from rice husk,then an alkaline treatment for the removal of hemicelluloses and lignin,and a two-step bleaching with hydrogen peroxide/tetra-acetylethylenediamine (TAED),followed by a mixture of acetic and nitric acids,for further delignification of the cellulose pulp.The techniques of infrared absorption spectroscopy (ATR-FTIR),scanning elec-tron microscopy (SEM),thermogravimetric analysis (TGA),modulated differential scanning calorimetry (MDSC)and X-ray diffraction (XRD)showed that the overall process is adequate to obtain cellulose with high purity and crystallinity.This cellulose was submitted to sulfuric acid hydrolysis with the aim to iso-late the whiskers.They showed the typical elongated rod-like aspect as revealed by transmission electron microscopy (TEM)and atomic force microscopy (AFM).© 2011 Elsevier Ltd. All rights reserved.1.IntroductionRice husk (RH)is one of the major agricultural residues gen-erated as a byproduct during the rice milling process.The Food and Agriculture Organization of the United Nations (FAO)forecasts that the global rice production stands at around 466million tonnes in 2010/2011(FAO,2010).About 23%of this amount consists of RH (Chandrasekhar,Satyanarayana,Pramada,Raghavan,&Gupta,2003).The Brazilian rice production has been in the order of 12mil-lion tonne/year and Rio Grande do Sul (the southernmost state of Brazil)is responsible for 60%of this production (IBGE,2010).Most of the RH produced is either used as a bedding material for animals and discarded in land fillings or simply burned in the fields lead-ing to air and soil pollution.The expressive content of about 20%silica in RH and,after burning,more than 90%silica in RH ash have stimulated extensive research which suggested the potential use of RH and its ash as sources of inorganic chemicals (Chandrasekhar et al.,2003).In the present work we propose the use of RH as a new source for obtaining cellulose whiskers and we employ a totally chlorine-free technique (TCF)to extract and bleach cellulose from RH.The isolation of highly pure cellulose from wheat straw (Sun,Sun,Su,&Sun,2004)and barley straw (Sun,Xu,Sun,Xiao,&Sun,2005)using totally chlorine-free technologies has been addressed in the scientific literature but not yet from rice husk.It is well known that the main components of plant fibers are cellulose,hemicelluloses and lignin.Cellulose,which awards the∗Corresponding author.Tel.:+555133087236;fax:+555133087304.E-mail address:claraism@iq.ufrgs.br (C.I.D.Bica).mechanical properties of these materials,is ordered in microfib-rils enclosed by the other two components,hemicellulose and lignin (Morán,Alvarez,Cyras,&Vazquez,2008).Cellulose is the most ubiquitous and abundant natural polymer on the planet,given its presence in plants and its widespread use for ropes,sails,paper,timber for housing and many other applications.By far,the most commercially exploited natural resource contain-ing cellulose is wood (Eichhorn et al.,2010)but cellulose is the main component of several other well employed natural fibers such as cotton,flax,hemp,jute and sisal (Morán et al.,2008).It is expected that the supply of wood at a reasonable price will be insufficient in the future and,apart from the natural fibers men-tioned above,agricultural byproducts will become more attractive as sources of cellulose (Leitner,Hinterstoisser,Wastyn,Keckes,&Gindl,2007).In recent years there has been a remarkable interest in cel-lulose fibers of nanometric dimensions.Cellulose whiskers and microfibrils are examples of nanocellulose and result from differ-ent isolation methods leading to diverse dimensions and aspect ratios (Siró&Plackett,2010).Cellulose whiskers are elongated crys-talline rod-like nanoparticles being generally isolated by means of acid hydrolysis which removes the amorphous domains existing in cellulose fibers.Cellulose microfibrils in turn are obtained from mechanical treatment being long and flexible nanoparticles which consist of alternating crystalline and amorphous strings (Siqueira,Bras,&Dufresne,2009).Cellulose whiskers have been isolated from different vegetable sources such as cotton and eucalyptus (Berg,Capadona,&Weder,2007;Dong,Revol,&Gray,1998;Hafraoui et al.,2008)and from animal sources such as tunicates (Berg et al.,2007;Hafraoui et al.,2008).Considering vegetable origin,there0144-8617/$–see front matter © 2011 Elsevier Ltd. All rights reserved.doi:10.1016/j.carbpol.2011.08.0841132S.M.L.Rosa et al./Carbohydrate Polymers87 (2012) 1131–1138are only a few papers which describe the isolation of whiskers from agricultural byproducts,as for example wheat straw(Herbert, Cavaillé,&Dufresne,1996),pea hullfiber(Chen,Liu,Chang,Cao, &Anderson,2009),branch-barks of mulberry(Li et al.,2009)and coconut husks(Rosa et al.,2010).As far as we know,the isolation of cellulose whiskers from rice husk sources has not been yet described in the literature but only the isolation of silicon carbide whiskers from RH(Sujiroti& Leangsuwan,2003)and of cellulose whiskers from rice straws(Orts et al.,2005).So,the fractionation of lignocellulosic materials of rice husks into its constitutive components by environmental friendly techniques has been the subject of our work with the objective of cellulose whisker isolation.RH and intermediate RH products of the multistep extraction procedure were characterized through scanning electron microscopy(SEM),thermogravimetry(TGA) and attenuated total reflectance-infrared absorption spectroscopy (ATR-FTIR).The purified cellulose was characterized by modu-lated differential scanning calorimetry(MDSC),wide-angle X-ray diffraction(WAXD)as well as TGA and ATR-FTIR.The whiskers were characterized by transmission electron microscopy(TEM)and atomic force microscopy(AFM).The properties of purified cellu-lose isolated from rice husk were compared to the properties of commercial microcrystalline cellulose(MCC).2.Experimental2.1.MaterialsRice husk was supplied by Engenho Meirebe(Eldorado do Sul/RS,Brazil).Hexane(Fmaia,Brazil),ethanol(Fmaia, Brazil),sodium hydroxide(Labsynth,Brazil),hydrogen perox-ide(CAQ Química,Brazil),nitric acid(Fmaia,Brazil),acetic acid (CAQ Química,Brazil),tetra-acetylethylenediamine(TAED)(Acros Organics,New Jersey,USA)were used as received.All solvents and reagents were of analytical grade.Microcrystalline cellulose(MCC) was supplied by Quimsul.2.2.Procedures2.2.1.Isolation of celluloseRice husks were previously ground.The dried RH was sequen-tially dewaxed with hexane/ethanol/water in a Soxhlet apparatus. The extractive content was found to be6.8%.Delignification was done at121◦C,in autoclave(Stermax20EHD),using a5%aqueous NaOH with a1:30straw to liquor ratio(g/mL)for30min being this step based on a procedure described by Uesu,Pineda,and Hechenleitner(2000),adapted to rice husk.The dispersions were treated with ultrasound for30min.In order to remove the remain-ing hemicelluloses and lignin,the resulting pulp was bleached following a procedure described by Sun,Sun,Su,et al.(2004):the pulp was treated with2%H2O2and0.2%TAED solution,at pH 11.8,for12h,at48◦C.The liquor to pulp ratio was25:1(mL/g). To purify the cellulose pulp,5.0mL of80%(v/v)acetic acid and 0.5mL of concentrated nitric acid(70%,v/v)were added to150mg of pulp,the mixture was then placed into a preheated oil bath at 120◦C,for15min or30min.Once cooled,the supernatant was then carefully decanted and the cellulose was washed sequentially with 95%ethanol(20mL),distilled water(20mL),and again95%ethanol (20mL)to remove extraction breakdown products and traces of nitric acid.Finally,the purified cellulose was dried in an oven at 60◦C until constant mass.Departing from raw rice husks(∼9wt% water),the total yield of extracted cellulose was28wt%.2.2.2.Isolation of the cellulose whiskersThe purified cellulose was mixed with sulfuric acid64%(w/w) at a ratio of1:8.75(g/mL)as described by Dong et al.(1998),at temperature of25◦C.The hydrolysis time wasfixed at60min. The reactions were stopped by pouring the mixture into a large amount of cold water.The excess of sulfuric acid was removed by centrifugation(3000rpm,30min),using an ALC centrifuge PK120, followed by a prolonged dialysis(regenerated cellulose membrane Fisher,cut-off10,000–14,000Da)against pure water.This proce-dure ensured that all ionic materials were removed except the H3O+ counterions associated with the sulfate groups on the surface of the whiskers(Dong et al.,1998).The whiskers were further dispersed by an ultrasonic treatment(Ultrasonic equipment Thornton,Model USC-1400).Although the strong nitric and sulfuric acids were used in the overall procedure,the effluents turned to be dilute and were easily neutralized.2.3.Characterization2.3.1.Rice husk and celluloseScanning electron micrographs of dried RH,extractive free and alkaline treated RH were obtained using a JEOL®microscope JSM 6060operating at20kV.The test specimens were attached to an aluminum stub and sputtered with gold to eliminate the electron charging effects.WAXD experiments were performed using a Siemens D-500 diffractometer.Purified RH cellulose(after30min bleaching and also called as RH cellulose)and MCC were scanned in the reflection mode using an incident X-ray of CuK␣with wavelength of1.54´˚A at a step width of0.05◦min−1from2Â=0to40◦.The Segal method was used to calculate the crystallinity of the samples(Thygesen, Oddershede,Lilholt,Thomsen,&Stahl,2005).Eq.(1)was used to calculate the sample crystallinity(X CR).X CR=I200−I AMI200×100%(1)where I200is the height of the200peak,which represents both crystalline and amorphous material and I AM is the lowest height between the200and110peaks,which represents amorphous material only.In our study we performed a preliminary experiment in a muffle furnace under air atmosphere to determine the ash content of rice husk.TGA scans were carried out from35to700◦C at a heating rate of10◦C min−1and under inert atmosphere of N2in aflux of 50mL min−1(TA Instruments model TGA Q5000IR).Sample weight was typically kept at17mg.The TGA microbalance has a precision of±0.1g.MDSC was performed using a DSC Q2000differential scan-ning calorimeter from TA Instruments.Sample weight was kept at ∼7mg using hermetically sealed pans with a pinhole in the lid.Two procedures were made using purified RH cellulose(after30min bleaching)in MDSC.In thefirst one,the samples were analysed as obtained after bleaching treatment,equilibrated at35◦C for5min and heated up to395◦C at heating rate of5◦C min−1.In addition,a second procedure was made applying a ramp of30◦C min−1from room temperature to150◦C and equilibrating at this temperature for5min to remove adsorbed water,as suggested in the literature (Cabrales&Abidi,2010;Picker&Hoag,2002).After this isothermal condition,samples were cooled until35◦C and a second scan was performed at5◦C min−1up to395◦C.The MDSC analyses were car-ried on under inert atmosphere of N2in aflux of50mL min−1using an amplitude of temperature modulation of±1◦C and a period modulation of60s.Structural changes between MCC,RH,RH intermediate prod-ucts and purified RH cellulose were revealed by using ATR-FTIR with64scans and a resolution of2cm−1,in a Nicolet6700 spectrophotometer.S.M.L.Rosa et al./Carbohydrate Polymers87 (2012) 1131–11381133Fig.1.ATR-FTIR spectra for RH,RH extractive-free,alkaline treated RH(RH after 15min autoclave),RH cellulose(after30min bleaching)and commercial cellulose (MCC)in the range from2000to800cm−1.2.3.2.Cellulose whiskersFor the TEM images,drops of RH whisker aqueous suspensions were deposited on glow-discharged carbon coated TEM grids and the excess of water was let to evaporate.The specimens were neg-atively stained with2%uranyl acetate and observed using a JEOL JEM1200FxII electron microscope operating at80kV.The whisker dimensions were determined with the aid of the Image Tools soft-ware.AFM observations were carried out using a Molecular Imag-ing Pico Plus microscope operating in air and intermittent contact mode with a Micromash NC36tip.Drops of dilute aqueous suspen-sions of RH cellulose whiskers were deposited onto freshly cleaved mica.After30min,the excess liquid was removed and the remain-ingfilm allowed to dry.3.Results and discussion3.1.Characterization of the rice husk and rice husk cellulose3.1.1.Spectroscopic characterizationFTIR spectroscopy has been extensively used in cellulose research,since it presents a relatively easy method of obtaining direct information on chemical changes that occur during various chemical treatments(Sun,Sun,Zhao,&Sun,2004).By identifying the functional groups present,FTIR allows to know about the chem-ical structure of each compound.In this work FTIR was employed with the aim of verifying if lignin and hemicelluloses were removed from the extracted cellulose.In this work FTIR spectra of RH,RH free of extractives,com-mercial cellulose(MCC),and purified RH cellulose were obtained. All samples presented two main absorbance regions.Thefirst one at high wavenumbers corresponds to the range2700–3500cm−1 (Fig.1S,Supplementary material),and the second one at lower wavenumbers,to the range800–1800cm−1approximately.The lat-al.,2008;Sun,Sun,Su,et al.,2004;Zuluaga,Putaux,Restrepo, Mondragon,&Ga˜nán,2007),this band relates to the bending mode of adsorbed water.All samples were carefully dried before the ATR-FTIR spectra were taken,but,as reported in the literature,it is difficult to completely dry cellulose due to its strong interaction with water(Morán et al.,2008;Szczesniak,Rachocki,&Tritt-Goc, 2008).All materials analysed presented this absorption band but specific absorptions can also be seen in the spectra.The absorp-tion band at1176cm−1corresponds to C–O–C asymmetrical bridge stretching.As pointed out by Sun,Sun,Su,et al.(2004),a strong peak at1049cm−1arises from C–O–C pyranose ring skeletal vibra-tion.In Fig.1it can be seen that this peak changes its form in the RH cellulose as far as it appears as a doublet.In comparison to the spectrum of commercial cellulose,it can be concluded that hemi-celluloses were extensively removed.The sharp peak at910cm−1 is characteristic of-glycosidic linkages between the sugar units (Sun,Sun,Su,et al.,2004).The spectra of RH and RH free of extrac-cial cellulose.According to Viera et al.(2007),the absence of these bands indicates that most of the lignin was removed.So in RH cel-lulose the extraction procedures removed most of lignin polymers because of the disappearance of the lignin-associated absorbances at1510cm−1and1244cm−1.In the spectrum it can also be identified a peak at1725cm−1which proba-bly arises from partial acetylation of RH the second bleaching step where acetic acid is employed as also mentioned by other authors(Morán et al.,2008;Sun,Sun,Su,et al.,2004;of RH and RH free of extrac-be seen which can also be assigned to hemicelluloses.Fig.1also shows ancellulose pulp obtained after 15min of alkaline treatment,in autoclave,and before the bleaching steps.In this spectrum there is not any absorbance in the carbonyl region.3.1.2.Scanning electron microscopy(SEM)By SEM it was possible to detect different effects on the RH sur-face according to the stages of pre-extraction and pulping,as shown in Fig.2.The changes in the outerattack suffered by the material at differentIn comparison to extractive-free rice huskof alkaline treatment in autoclave,it can be seenparticles changed fromflat to rolled shape(Fig.the surface of extractive-free rice husk withica particles.A similar aspect of RH surface wasChandrasekhar et al.(2003).Fig.2d shows thatremoved after15min in autoclave.In Fig.2efilaments can be seen on the outer epidermis in the regions where protuberances were removed after30min in autoclave.Fig.2f shows that after1h in autoclave the surface did not change significantly.So30min in autoclave was chosen as the optimum time.By comparing Fig.2g (15min in autoclave)and Fig.2h(30min in autoclave)it can be noticed that the inner epidermis is also modified when the auto-clave treatment is increased to30min.This alkaline treatment in autoclave also causes a reduction of the average size of RH particles (Fig.2S,Supplementary material).3.1.3.Thermogravimetric analysis(TGA)Fig.3shows the thermal degradation pattern of the commer-cial cellulose(MCC),crude RH,and RH cellulose(after15min and 30min bleaching).All samples showed a thermal event below 150◦C corresponding to dehydration.The mass loss of water in this step was determined from45◦C to150◦C.It was about3.8wt%for1134S.M.L.Rosa et al./Carbohydrate Polymers 87 (2012) 1131–1138Fig.2.SEM micrographs of RH after various stages of chemical attack:a,b)outer epidermis of RH extractive-free (bars:200m and 10m,respectively);c,d)RH outer epidermis after 15min in autoclave (100m and 10m,respectively);e)RH outer epidermis after 30min in autoclave (bar:10m,both);f)RH outer epidermis after 60min in autoclave (bar:10m);g)RH inner epidermis after 15min in autoclave (bar:10m);h)RH inner epidermis after 30min in autoclave (bar:10m).MCC,9.0wt%for crude RH,5.8wt%for RH cellulose after 15min bleaching and 5.7wt%for RH cellulose after 30min bleaching.The effective thermal degradation of the RH constituents begins above 200◦C and refers to bond cleavage of hemicellulose,cellulose and lignin.It is possible to verify that RH cellulose showed higher ther-mal stability than the precursor RH,since in these samples the components that start to degrade at lower temperature had been removed.The crude RH main decomposition peak is considerably wider than those of the other samples due to the decomposition of hemicelluloses and mercial cellulose and RH cellulose decomposed in a single step.This behavior suggests the absence of hemicellulose and lignin in the RH cellulose obtained.The DTG curve of RH cellulose does not show the shoulder close to the cellu-lose peak that refers to the hemicellulose.This is in accordance with the FTIR results previously shown.The maximum rate of decompo-sition of RH cellulose occurred at 345◦C.This temperature agrees well with the value of 348◦C found by Morán et al.(2008)fortheFig.3.DTGA curves for commercial cellulose (MCC),RH,RH cellulose after 15min bleaching and RH cellulose (30min bleaching).decomposition peak of commercial cellulose and 355◦C found by Yang,Yan,Chen,Lee,&Zheng (2007),determined at same heat-ing rate.The commercial cellulose showed higher T max than the RH cellulose isolated in this step.According to the literature,the higher the decomposition temperature obtained by thermogravi-metric analysis the greater the crystallinity of cellulose (Alemdar &Sain,2008;Chen et al.,2011;Uesu,Pineda,&Hechenleitner,2000).However,the discussions have been recently improved considering other effects that can influence the temperature peak of degrada-tion:presence of substances bonded to microfibril surfaces (Vila,Barneto,Fillat,Vidal,&Ariza,2011),crystal size of cellulose (Kim,Eom,&Wada,2010)and the atmosphere environment used (usu-ally nitrogen or air)(Mamleev,Bourbigot,&Yvon,2007;Vila et al.,2011).RH presented a high residual mass at the end of the experi-ment (700◦C),around 26%.The ash content of rice husk determined under air atmosphere in this work was 16wt%at 1000◦C.The result agrees perfectly well with Zhao et al.(2009).Even considering that the analysis was performed under nitrogen atmosphere,this was an especially high value and it was related to the high silica con-tent of RH (Rosa,Nachtigall,&Ferreira,2009).At 700◦C residues of about 8%for commercial cellulose,15%for RH cellulose after 15min bleaching and 11%for RH cellulose after 30min bleaching can be determined from the TGA curves (Fig.3S,Supplementary material ).As indeed evidenced by the X-ray diffraction study,the crystallinity index of RH cellulose is lower than that of the commercial cellulose.Another explanation may be related to the partial acetylation of RH cellulose evidenced by the presence of an absorption at 1725cm −1in the ATR-FTIR spectrum.3.1.4.Modulated differential scanning calorimetry (MDSC)Modulated differential scanning calorimetry (MDSC)permits the separation of the total heat flow signal into its reverse heat flow and non-reverse heat flow components.The separation is based not only on thermodynamic reversibility but also on changes occurring when a sinusoidal modulation is overlaid on a conventional linear heating rate during an experiment.In this sense,MDSC arises as an exciting way to increase the understanding of rice husk cellulose thermal properties.The effects of temperature on amorphous and crystalline regions of rice husk cellulose were studied by MDSC.S.M.L.Rosa et al./Carbohydrate Polymers87 (2012) 1131–11381135Fig.4.MDSC curves of total(1),reverse(2)and non-reverse(3)heatflow at5◦C min−1:(a)RH cellulose(30min bleaching),underfirst procedure;(b)RH cellulose(30min bleaching),under second procedure;(c)MCC,underfirst procedure;(d)MCC,under second procedure.Considering literature using DSC technique,as reported by Morán et al.(2008)and Yang et al.(2007),the fusion of the crystalline fraction of some types of cellulose shows a narrow endothermic peak close to330◦C.This transition can move to lower temperatures depending on factors such as molecular weight, amount of amorphous content,crystallite sizes,etc.Sometimes, an exothermic peak is found in the same region,which has been related to a degradation process(Morán et al.,2008).According to Mamleev et al.’s studies(2007),a depolymerization by transglyco-sylation occurs at310◦C during cellulose pyrolysis.As both events can be superimposed,they cannot be easily distinguished in many cases.Fig.4a shows the heatflow curves of RH cellulose analysed by MDSC.Considering total and non-reverse heatflow curves,they show two main events.Thefirst endothermic peak observed below 150◦C is due to loss of water.The second endothermic transition starts around270◦C with a peak at320◦C and is related to cel-lulose melting.A smooth exothermic transition can be detected near340◦C.This event has its onset overlapped with the end of the endothermic region and can be related to the depolymerization of cellulose as supported by the equivalent peak in the non-reverse heating curve.Such conclusion is also corroborated by the TGA study which shows a maximum of weight loss for RH cellulose in the same temperature region.On the other hand,an important change in the heat capacity of the medium can also be seen between300◦C and330◦C in the reverse heatflow curve.This indicates a change in chemical composition as a result of the depolymerization reac-tion.The absence of an endotherm in reversing signal indicates that this thermal event is a kinetic transformation.By visual inspection of the pan,very few solid residues were found at this stage and charring process was evident.Fig.4b shows the MDSC curves of RH cellulose submitted to the second procedure described in the experimental section,with an isothermal step to eliminate water.As expected,it was not found any peak due to water release.A well-defined endothermic tran-sition is present beyond300◦C which is similar to that of Fig.4a being related to melting and volatilization as well.However the small exothermic peak following this transition was not clearly seen in the total and non-reverse curves.The thermograms profiles of RH cellulose are very similar to those of MCC which are shown in Fig.4c and d.In comparison to MCC,the peak maximum of the endothermic transition detected beyond300◦C occurred at lower temperature for RH cellulose(as assigned by arrows T RH=321◦C, in Fig.4a and b,and T MCC=344◦C in Fig.4c and d)independently of water presence as it was observed in total and non-reverse heating curves.In this study,it was observed that all samples showed well-defined endothermic peaks corresponding to the fusion of its crystalline part,as shown in Fig.4a–d.However,cellulose sam-ples with water adsorbed(Fig.4a and c)showed more clearly the exothermic peaks following melting.This suggests that the degra-dation mechanism responsible for the exothermic peak is affected by the presence of water.3.1.5.Wide angle X-ray diffraction(WAXD)It can be observed in Fig.5that the major crystalline peak for each sample occurred at around2Â=22◦which represents the cellulose crystallographic plane(200).The crystallinity index of1136S.M.L.Rosa et al./Carbohydrate Polymers 87 (2012) 1131–1138Fig.5.X-ray diffraction patterns of MCC and RH cellulose (30min bleaching).RH cellulose (calculated by Segal formula)was approximately 67%while that of MCC was estimated as 79%.For comparison,the crys-tallinity index of other samples,as reported in the literature,was found to be around 66%for potato tuber cellulose,68%for rice straw cellulose and 71%for wood cellulose (Abe &Yano,2009).It can be concluded that the procedure employed in this study for cel-lulose extraction from rice husk is adequate for obtaining samples with high crystallinity.It was reported that highly crystalline fibers fibril aggregates could be more effective in achieving higher reinforcement for composite materials (Cheng,Wang,Rials,&Lee,2007).In addition it can be noticed in Fig.5that RH cellulose can be classified as cellulose I,since there is no doublet in the intensity of the peak at ca.2Â=22◦.A similar finding was reported by Morán et al.(2008)for sisal cellulose extracted by other procedures.3.2.Characterization of cellulose whiskersBasically,microscopy has been the preferred technique for the morphological characterization in studies involving cellulose whiskers.In this study,AFM and TEM were used to investigate the morphology and size of the dispersed structures.The atomic force micrograph in Fig.6shows the sample obtained after 60min of hydrolysis.It was possible to see the isolated cellu-lose fibrils free from the other components of rice husks.Most ofFig.6.AFM image of RH cellulose whiskers obtained after 60min of acid hydrolysis.the hydrogen bonds that kept the whiskers associated were prob-ably disrupted after this procedure.However,some aggregates are still present.By TEM (Fig.7a and b),structures in the form needles rang-ing from 100to 400nm in length and 6to 14nm in width were observed.The average length value was L =(143±64)nm while the average thickness was d =(8±2)nm.Such dimensions are compara-ble to those of whiskers originating from cotton (Beck-Candanedo,Roman,&Gray,2005;Bica,Borsali,Rochas,&Geissler,2006;Hafraoui et al.,2008),wood (Beck-Candanedo et al.,2005),pea hull fiber (Chen et al.,2009)and coconut husks (Rosa et al.,2010).The RH whiskers show lengths shorter than in the case of branch-barks of mulberry (Li et al.,2009)but RH whiskers are much thinner.The aspect ratio shows an average value near 18.In Fig.6some RH whiskers appeared more aggregated in the form of bundles as also observed by Heux,Chauve,and Bonini (2000)in the case of cotton whiskers.According to Hafraoui et al.(2008),such nanostructures can be composed of a varying number of parallel subunits of cellu-lose chains.The high aspect ratio of the cellulose whiskers obtained from rice husk indicates that these structures exhibit promisingFig.7.TEM images of RH cellulose whiskers (bars correspond to 100nm).。