CN103861567A - Preparation method of hydroxyapatite/bagasse active carbon - Google Patents
Preparation method of hydroxyapatite/bagasse active carbon Download PDFInfo
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- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims abstract description 37
- 241000609240 Ambelania acida Species 0.000 title claims abstract description 36
- 239000010905 bagasse Substances 0.000 title claims abstract description 36
- 229910052588 hydroxylapatite Inorganic materials 0.000 title claims abstract description 30
- XYJRXVWERLGGKC-UHFFFAOYSA-D pentacalcium;hydroxide;triphosphate Chemical compound [OH-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O XYJRXVWERLGGKC-UHFFFAOYSA-D 0.000 title claims abstract description 29
- 238000002360 preparation method Methods 0.000 title claims abstract description 6
- 229910052799 carbon Inorganic materials 0.000 title 1
- 239000000203 mixture Substances 0.000 claims abstract description 13
- 238000003756 stirring Methods 0.000 claims abstract description 12
- 239000000243 solution Substances 0.000 claims abstract description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 9
- USFZMSVCRYTOJT-UHFFFAOYSA-N Ammonium acetate Chemical compound N.CC(O)=O USFZMSVCRYTOJT-UHFFFAOYSA-N 0.000 claims abstract description 6
- 239000005695 Ammonium acetate Substances 0.000 claims abstract description 6
- 229940043376 ammonium acetate Drugs 0.000 claims abstract description 6
- 235000019257 ammonium acetate Nutrition 0.000 claims abstract description 6
- VSGNNIFQASZAOI-UHFFFAOYSA-L calcium acetate Chemical compound [Ca+2].CC([O-])=O.CC([O-])=O VSGNNIFQASZAOI-UHFFFAOYSA-L 0.000 claims abstract description 6
- 235000011092 calcium acetate Nutrition 0.000 claims abstract description 6
- 239000001639 calcium acetate Substances 0.000 claims abstract description 6
- 229960005147 calcium acetate Drugs 0.000 claims abstract description 6
- LFVGISIMTYGQHF-UHFFFAOYSA-N ammonium dihydrogen phosphate Chemical compound [NH4+].OP(O)([O-])=O LFVGISIMTYGQHF-UHFFFAOYSA-N 0.000 claims abstract description 5
- 229910000387 ammonium dihydrogen phosphate Inorganic materials 0.000 claims abstract description 5
- 235000019837 monoammonium phosphate Nutrition 0.000 claims abstract description 5
- 239000007853 buffer solution Substances 0.000 claims abstract description 4
- 239000000047 product Substances 0.000 claims description 11
- 239000002131 composite material Substances 0.000 claims description 6
- 239000011521 glass Substances 0.000 claims description 6
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims description 3
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 3
- 235000011114 ammonium hydroxide Nutrition 0.000 claims description 3
- 238000006243 chemical reaction Methods 0.000 claims description 3
- 239000012065 filter cake Substances 0.000 claims description 3
- 239000000706 filtrate Substances 0.000 claims description 3
- 229910052573 porcelain Inorganic materials 0.000 claims description 3
- 239000002244 precipitate Substances 0.000 claims description 3
- 239000007790 solid phase Substances 0.000 claims description 3
- 229910021642 ultra pure water Inorganic materials 0.000 claims description 3
- 239000012498 ultrapure water Substances 0.000 claims description 3
- 238000000034 method Methods 0.000 abstract description 8
- 239000002351 wastewater Substances 0.000 abstract description 5
- 238000005065 mining Methods 0.000 abstract description 2
- 239000000725 suspension Substances 0.000 abstract 2
- ZIXVIWRPMFITIT-UHFFFAOYSA-N cadmium lead Chemical compound [Cd].[Pb] ZIXVIWRPMFITIT-UHFFFAOYSA-N 0.000 abstract 1
- 238000001179 sorption measurement Methods 0.000 description 17
- 229910052793 cadmium Inorganic materials 0.000 description 15
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 15
- 229910001385 heavy metal Inorganic materials 0.000 description 8
- 239000003463 adsorbent Substances 0.000 description 7
- 239000000463 material Substances 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 210000000988 bone and bone Anatomy 0.000 description 2
- WLZRMCYVCSSEQC-UHFFFAOYSA-N cadmium(2+) Chemical compound [Cd+2] WLZRMCYVCSSEQC-UHFFFAOYSA-N 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 230000006378 damage Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 229910052598 goethite Inorganic materials 0.000 description 2
- AEIXRCIKZIZYPM-UHFFFAOYSA-M hydroxy(oxo)iron Chemical compound [O][Fe]O AEIXRCIKZIZYPM-UHFFFAOYSA-M 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 238000005342 ion exchange Methods 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 210000003734 kidney Anatomy 0.000 description 2
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 239000004408 titanium dioxide Substances 0.000 description 2
- 235000017060 Arachis glabrata Nutrition 0.000 description 1
- 241001553178 Arachis glabrata Species 0.000 description 1
- 235000010777 Arachis hypogaea Nutrition 0.000 description 1
- 235000018262 Arachis monticola Nutrition 0.000 description 1
- 229910014497 Ca10(PO4)6(OH)2 Inorganic materials 0.000 description 1
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical group [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 description 1
- CUPCBVUMRUSXIU-UHFFFAOYSA-N [Fe].OOO Chemical compound [Fe].OOO CUPCBVUMRUSXIU-UHFFFAOYSA-N 0.000 description 1
- JAQXDZTWVWLKGC-UHFFFAOYSA-N [O-2].[Al+3].[Fe+2] Chemical class [O-2].[Al+3].[Fe+2] JAQXDZTWVWLKGC-UHFFFAOYSA-N 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 208000007502 anemia Diseases 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 229910052586 apatite Inorganic materials 0.000 description 1
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical class O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000001506 calcium phosphate Substances 0.000 description 1
- 229910000389 calcium phosphate Inorganic materials 0.000 description 1
- 235000011010 calcium phosphates Nutrition 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 238000000975 co-precipitation Methods 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 210000002249 digestive system Anatomy 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical class O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- -1 fluoride ions Chemical class 0.000 description 1
- 239000011737 fluorine Substances 0.000 description 1
- 229910052731 fluorine Inorganic materials 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 210000000777 hematopoietic system Anatomy 0.000 description 1
- 238000001027 hydrothermal synthesis Methods 0.000 description 1
- 229910052900 illite Inorganic materials 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 210000000936 intestine Anatomy 0.000 description 1
- 229910021519 iron(III) oxide-hydroxide Inorganic materials 0.000 description 1
- 230000003902 lesion Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical class C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 1
- 210000000653 nervous system Anatomy 0.000 description 1
- VGIBGUSAECPPNB-UHFFFAOYSA-L nonaaluminum;magnesium;tripotassium;1,3-dioxido-2,4,5-trioxa-1,3-disilabicyclo[1.1.1]pentane;iron(2+);oxygen(2-);fluoride;hydroxide Chemical compound [OH-].[O-2].[O-2].[O-2].[O-2].[O-2].[F-].[Mg+2].[Al+3].[Al+3].[Al+3].[Al+3].[Al+3].[Al+3].[Al+3].[Al+3].[Al+3].[K+].[K+].[K+].[Fe+2].O1[Si]2([O-])O[Si]1([O-])O2.O1[Si]2([O-])O[Si]1([O-])O2.O1[Si]2([O-])O[Si]1([O-])O2.O1[Si]2([O-])O[Si]1([O-])O2.O1[Si]2([O-])O[Si]1([O-])O2.O1[Si]2([O-])O[Si]1([O-])O2.O1[Si]2([O-])O[Si]1([O-])O2 VGIBGUSAECPPNB-UHFFFAOYSA-L 0.000 description 1
- 229920000620 organic polymer Polymers 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 235000020232 peanut Nutrition 0.000 description 1
- VSIIXMUUUJUKCM-UHFFFAOYSA-D pentacalcium;fluoride;triphosphate Chemical compound [F-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O VSIIXMUUUJUKCM-UHFFFAOYSA-D 0.000 description 1
- 239000012071 phase Substances 0.000 description 1
- 238000013033 photocatalytic degradation reaction Methods 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 210000004994 reproductive system Anatomy 0.000 description 1
- 238000001878 scanning electron micrograph Methods 0.000 description 1
- 238000004626 scanning electron microscopy Methods 0.000 description 1
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- 239000010802 sludge Substances 0.000 description 1
- 238000000638 solvent extraction Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- QORWJWZARLRLPR-UHFFFAOYSA-H tricalcium bis(phosphate) Chemical compound [Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O QORWJWZARLRLPR-UHFFFAOYSA-H 0.000 description 1
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Abstract
本发明公开了一种羟基磷灰石/蔗渣活性炭的制备方法。在250ml0.05mol/L~0.5mol/L的醋酸钙溶液中加入4.4mol/L醋酸铵缓冲溶液250ml,混合均匀,再加入10~60克甘蔗渣,电动搅拌后,用超声波振荡30~60分钟,静置24~48小时;在快速搅拌下向醋酸钙、醋酸铵和甘蔗渣混合物中加入500ml0.015mol/L~0.15mol/L磷酸二氢铵溶液,调节pH值到7.5~8.0,室温下搅拌10分钟;水浴加热到100℃,反应48~60小时,得羟基磷灰石/蔗渣混合悬浮物溶液;自然冷却,过滤,洗涤后,在70℃下干燥16小时,羟基磷灰石/蔗渣混合物;在450℃~650℃下进行炭化,然后研磨,过100目筛。本发明工艺简单、成本低;所制得的产品可广泛应用于工矿企业深度处理含镉和铅废水工序。
The invention discloses a preparation method of hydroxyapatite/bagasse activated carbon. Add 250ml of 4.4mol/L ammonium acetate buffer solution to 250ml of 0.05mol/L~0.5mol/L calcium acetate solution, mix well, then add 10~60g of bagasse, after electric stirring, use ultrasonic vibration for 30~60 minutes , let it stand for 24~48 hours; add 500ml0.015mol/L~0.15mol/L ammonium dihydrogen phosphate solution to the mixture of calcium acetate, ammonium acetate and bagasse under rapid stirring, adjust the pH value to 7.5~8.0, at room temperature Stir for 10 minutes; heat in a water bath to 100°C and react for 48-60 hours to obtain a mixed suspension solution of hydroxyapatite/bagasse; naturally cool, filter, wash, and dry at 70°C for 16 hours to obtain a mixed suspension of hydroxyapatite/bagasse Mixture; carbonized at 450°C~650°C, then ground and passed through a 100-mesh sieve. The process of the invention is simple and the cost is low; the prepared product can be widely used in the process of advanced treatment of cadmium- and lead-containing wastewater in industrial and mining enterprises.
Description
技术领域 technical field
本发明涉及一种羟基磷灰石/蔗渣活性炭的制备方法。 The invention relates to a preparation method of hydroxyapatite/bagasse activated carbon.
背景技术 Background technique
随着现代工业的快速发展,含有镉和铅的重金属废水排放量越来越大,重金属的污染已成为最严重的环境问题之一,因此,对含有镉和铅的重金属废水的处理刻不容缓。在众多重金属中,镉离子是毒性最大、危害人体健康最严重的重金属离子之一,当镉离子在人体中积累到一定剂量时,就易引起人体肾、肠、骨骼的病变。而铅离子对人体的危害是相当广泛的,人体若是摄入过量的铅会造成铅性贫血以及神经系统、骨骼造血系统、消化系统、肾脏及生殖系统的严重损害。当前处理含有镉和铅重金属废水的方法主要有共沉淀法、絮凝法、氧化还原法、光催化降解法、离子交换法、溶剂萃取法、吸附法、膜分离法等。化学沉淀法会产生大量含重金属的剩余污泥,提高了处理成本,镉和铅的回收也有一定的困难,离子交换法的处理成本亦较高。近年来,很多研究者将吸附法除镉和铅作为一个研究方向。常用的吸附剂有:活性炭、羟基氧化铁、针铁矿、二氧化钛和活性氧化铝等,但是此类吸附剂多为粉末状,虽然比表面积大,但吸附量还是比较低。 With the rapid development of modern industry, the discharge of heavy metal wastewater containing cadmium and lead is increasing, and the pollution of heavy metals has become one of the most serious environmental problems. Therefore, the treatment of heavy metal wastewater containing cadmium and lead is urgent. Among the many heavy metals, cadmium ions are one of the most toxic and most harmful to human health. When cadmium ions accumulate in the human body to a certain dose, it is easy to cause lesions in the kidneys, intestines, and bones of the human body. The harm of lead ions to the human body is quite extensive. If the human body takes too much lead, it will cause lead anemia and serious damage to the nervous system, bone hematopoietic system, digestive system, kidney and reproductive system. The current methods for treating heavy metal wastewater containing cadmium and lead mainly include co-precipitation, flocculation, redox, photocatalytic degradation, ion exchange, solvent extraction, adsorption, membrane separation, etc. The chemical precipitation method will produce a large amount of excess sludge containing heavy metals, which increases the treatment cost. There are also certain difficulties in the recovery of cadmium and lead, and the treatment cost of the ion exchange method is also relatively high. In recent years, many researchers have taken the removal of cadmium and lead by adsorption as a research direction. Commonly used adsorbents are: activated carbon, iron oxyhydroxide, goethite, titanium dioxide, and activated alumina, etc., but most of these adsorbents are in the form of powders. Although the specific surface area is large, the adsorption capacity is still relatively low.
磷灰石是自然界广泛存在的磷酸钙盐矿物,根据其内部存在的阴离子的种类,可分为氟、氯、羟基磷灰石等不同亚种矿物。其中,羟基磷灰石的研究和应用最广泛。羟基磷灰石的分子式为Ca10(PO4)6(OH)2,为六方晶系,这种晶体化学特征,使得不同类型的重金属能够取代羟基磷灰石中钙的位置,具有良好的离子吸附和交换特性,能吸附回收地下水中的氟离子、工业废水中的重金属以及有机高分子,并且羟基磷灰石与环境具有良好协调性,不易造成二次污染,从而成为一种备受关注的新型环境吸附材料。有大量文献资料显示,羟基磷灰石对镉和铅的去除效果显著。活性炭是一种性能优良的吸附剂,但其对镉和铅的吸附效果有限。因此,如何把两种具有优良吸附性能的吸附剂有机结合在一起,使其吸附性能达到取长补短的效果,是目前研究的一个热点问题。因此,以甘蔗渣为主要原料,制备羟基磷灰石/蔗渣活性炭复合吸附剂具有较为有利的发展前景及实用意义。 Apatite is a calcium phosphate mineral that exists widely in nature. According to the types of anions in it, it can be divided into different subspecies of minerals such as fluorine, chlorine, and hydroxyapatite. Among them, the research and application of hydroxyapatite are the most extensive. The molecular formula of hydroxyapatite is Ca 10 (PO 4 ) 6 (OH) 2 , which is a hexagonal crystal system. This crystal chemical feature enables different types of heavy metals to replace the calcium in hydroxyapatite, and has a good ion Adsorption and exchange characteristics, can absorb and recover fluoride ions in groundwater, heavy metals in industrial wastewater and organic polymers, and hydroxyapatite has good coordination with the environment, and is not easy to cause secondary pollution, so it has become a concern New environmental adsorption material. A large amount of literature shows that hydroxyapatite has a significant effect on the removal of cadmium and lead. Activated carbon is an excellent adsorbent, but its adsorption effect on cadmium and lead is limited. Therefore, how to organically combine two kinds of adsorbents with excellent adsorption properties so that the adsorption properties can achieve the effect of complementing each other is a hot issue in current research. Therefore, the preparation of hydroxyapatite/bagasse activated carbon composite adsorbent with bagasse as the main raw material has favorable development prospects and practical significance.
发明内容 Contents of the invention
本发明的目的就是提供一种在常压下采用水热合成法和煅烧法,以甘蔗渣为主要原料,以醋酸钙、醋酸铵和磷酸二氢铵为辅助材料,制备羟基磷灰石/蔗渣活性炭复合吸附剂。 The purpose of the present invention is to provide a method of hydrothermal synthesis and calcination under normal pressure, using bagasse as the main raw material, and calcium acetate, ammonium acetate and ammonium dihydrogen phosphate as auxiliary materials to prepare hydroxyapatite/bagasse Activated carbon composite adsorbent.
目前,研究较多的吸附除镉和铅的吸附材料中,单一的物质有水合二氧化锰、针铁矿、活性炭纤维、二氧化钛和纳米金属铝粉等;复合的物质有改性膨润土、改性沸石、伊利石、改性花生壳、草木灰、风化煤等。这些吸附材料中有的吸附材料的主要成分是铁铝氧化物,它们也是吸附镉和铅的主要物质,而部分吸附材料中的主要成分是活性炭等一些有机物质。为了克服现有的除镉和铅吸附剂吸附容量低,吸附能力有限,以及充分利用广西丰富的甘蔗渣资源。本发明提供一种除镉和铅吸附材料——羟基磷灰石/蔗渣活性炭的制备方法。羟基磷灰石/蔗渣活性炭不仅能使处理后含镉和铅水样的镉和铅浓度均低于0.050 mg·L-1,而且吸附容量大,当含镉和铅水样初始浓度分别为低于5.0 mg·L-1。吸附平衡后水样中镉和铅浓度低于0.01 mg·L-1。 At present, among the adsorption materials that have been studied more for the adsorption and removal of cadmium and lead, the single substances include hydrated manganese dioxide, goethite, activated carbon fiber, titanium dioxide and nano-metal aluminum powder, etc.; the composite substances include modified bentonite, modified Zeolite, illite, modified peanut shells, plant ash, weathered coal, etc. The main components of some of these adsorption materials are iron-aluminum oxides, which are also the main substances for adsorbing cadmium and lead, while the main components of some adsorption materials are some organic substances such as activated carbon. In order to overcome the low adsorption capacity and limited adsorption capacity of the existing cadmium and lead adsorbents, and make full use of the abundant bagasse resources in Guangxi. The invention provides a preparation method of cadmium and lead adsorption material-hydroxyapatite/bagasse activated carbon. Hydroxyapatite/bagasse activated carbon can not only reduce the concentration of cadmium and lead in water samples containing cadmium and lead after treatment to less than 0.050 mg·L -1 , but also has a large adsorption capacity. at 5.0 mg·L -1 . The concentrations of cadmium and lead in water samples after adsorption equilibrium were lower than 0.01 mg·L -1 .
具体步骤为: The specific steps are:
(1)将甘蔗渣置于烘箱中在80℃下烘干,破碎后过20目筛备用。 (1) Dry the bagasse in an oven at 80°C, crush it and pass it through a 20-mesh sieve for later use.
(2)于2L烧杯中加入250 ml 浓度为0.05 mol/L~0.5 mol/L的醋酸钙溶液,再加入250 ml 浓度为4.4 mol/L醋酸铵缓冲溶液,混合均匀,加入10~60克步骤(1)所得甘蔗渣,电动搅拌后,用超声波振荡30~60分钟,静置24~48小时。 (2) Add 250 ml of calcium acetate solution with a concentration of 0.05 mol/L to 0.5 mol/L in a 2L beaker, then add 250 ml of ammonium acetate buffer solution with a concentration of 4.4 mol/L, mix well, and add 10 to 60 grams of The bagasse obtained in step (1) is electrically stirred, then ultrasonically oscillated for 30-60 minutes, and left to stand for 24-48 hours.
(3)在快速搅拌下向步骤(2)产物中加入500ml 浓度为0.015mol/L~ 0.15mol/L 磷酸二氢铵溶液,用全自动滴定仪,在搅拌下,缓慢加入质量百分比浓度为10%的氨水小心调节反应的pH值到7.5~8.0,室温下搅拌10分钟。 (3) Add 500ml of ammonium dihydrogen phosphate solution with a concentration of 0.015mol/L~0.15mol/L to the product of step (2) under rapid stirring, and slowly add it with a concentration of 10% by mass under stirring with an automatic titrator. % ammonia water to carefully adjust the pH value of the reaction to 7.5-8.0, and stir at room temperature for 10 minutes.
(4)将步骤(3)所得产物置于恒温水浴上中,盖好玻璃表面皿,水浴加热到100℃,反应48~60小时。 (4) Place the product obtained in step (3) in a constant temperature water bath, cover the glass watch glass, heat the water bath to 100°C, and react for 48-60 hours.
(5)将步骤(4)所得产物自然冷却,过滤,测定并记录滤液最终pH值。固相沉淀物经超纯水反复洗涤两次后,再用无水乙醇洗涤一遍,滤饼置于瓷盘中在70℃下干燥16小时,得羟基磷灰石/蔗渣混合物。 (5) Cool the product obtained in step (4) naturally, filter, measure and record the final pH value of the filtrate. The solid-phase precipitate was repeatedly washed twice with ultrapure water, and then washed once with absolute ethanol, and the filter cake was placed in a porcelain plate and dried at 70°C for 16 hours to obtain a hydroxyapatite/bagasse mixture.
(6)将步骤(5)所得羟基磷灰石/蔗渣混合物在450℃~650℃下进行炭化,得羟基磷灰石/蔗渣活性炭复合物;然后研磨,过100目筛,得羟基磷灰石/蔗渣活性炭。 (6) Carbonize the hydroxyapatite/bagasse mixture obtained in step (5) at 450°C to 650°C to obtain a hydroxyapatite/bagasse activated carbon composite; then grind and pass through a 100-mesh sieve to obtain hydroxyapatite / Bagasse Activated Carbon.
本发明工艺简单易行,由于利用甘蔗渣为主要原材料,大大降低生产成本,并提高了产品各项性能指标;所制得的产品可广泛应用于工矿企业深度处理含镉和铅废水工序。 The process of the invention is simple and easy, and since the bagasse is used as the main raw material, the production cost is greatly reduced, and various performance indexes of the product are improved; the prepared product can be widely used in industrial and mining enterprises for advanced treatment of waste water containing cadmium and lead.
附图说明Description of drawings
图1、图2、图3为本发明实施例所制得的羟基磷灰石/蔗渣活性炭的扫描电镜图。 Fig. 1, Fig. 2, Fig. 3 are the scanning electron micrographs of the hydroxyapatite/bagasse activated carbon prepared in the embodiment of the present invention.
具体实施方式 Detailed ways
实施例: Example:
(1)将甘蔗渣置于烘箱中在80℃下烘干,用万能破碎机破碎后过20目筛备用。 (1) Dry the bagasse in an oven at 80°C, crush it with a universal crusher and pass it through a 20-mesh sieve for later use.
(2)于2L烧杯中加入250 ml 浓度为0.2 mol/L的醋酸钙溶液,再加入250 ml 浓度为4.4 mol/L醋酸铵缓冲溶液,混合均匀,加入50克步骤(1)所得甘蔗渣,电动搅拌后,用超声波振荡30分钟,静置24小时。 (2) Add 250 ml of calcium acetate solution with a concentration of 0.2 mol/L to a 2L beaker, then add 250 ml of ammonium acetate buffer solution with a concentration of 4.4 mol/L, mix well, and add 50 grams of bagasse obtained in step (1) , after electric stirring, oscillate ultrasonically for 30 minutes, and let stand for 24 hours.
(3)在快速搅拌下向步骤(2)所得产物中加入500ml 浓度为0.06mol/L 磷酸二氢铵溶液,用全自动滴定仪,在搅拌下,缓慢加入质量百分比浓度为10%的氨水小心调节反应的pH值到7.5,室温下搅拌10分钟。 (3) Add 500ml ammonium dihydrogen phosphate solution with a concentration of 0.06mol/L to the product obtained in step (2) under rapid stirring, and use an automatic titrator to slowly add ammonia water with a mass percentage concentration of 10% under stirring. The pH of the reaction was adjusted to 7.5 and stirred at room temperature for 10 minutes.
(4)将步骤(3)所得产物置于恒温水浴上中,盖好玻璃表面皿,水浴加热到100℃,反应48小时。 (4) Place the product obtained in step (3) in a constant temperature water bath, cover the glass watch glass, heat the water bath to 100°C, and react for 48 hours.
(5)将步骤(4)所得产物自然冷却,过滤,测定并记录滤液最终pH值。固相沉淀物经超纯水反复洗涤两次后,再用无水乙醇洗涤一遍,滤饼置于瓷盘中在70℃下干燥16小时,得羟基磷灰石/蔗渣混合物。 (5) Cool the product obtained in step (4) naturally, filter, measure and record the final pH value of the filtrate. The solid-phase precipitate was repeatedly washed twice with ultrapure water, and then washed once with absolute ethanol. The filter cake was placed in a porcelain plate and dried at 70° C. for 16 hours to obtain a hydroxyapatite/bagasse mixture.
(6)将步骤(5)所得羟基磷灰石/蔗渣混合物在600℃下进行炭化,得羟基磷灰石/蔗渣活性炭复合物;然后研磨,过100目筛,羟基磷灰石/蔗渣活性炭。 (6) Carbonize the hydroxyapatite/bagasse mixture obtained in step (5) at 600°C to obtain a hydroxyapatite/bagasse activated carbon composite; then grind and pass through a 100-mesh sieve to obtain hydroxyapatite/bagasse activated carbon.
所制得的羟基磷灰石/蔗渣活性炭的物相与结构、成分组成则采用德国Bruker-axs D8ADVANCE 型X射线衍射仪进行测试,衍射角范围2θ=10-90°,衍射速率4°/分钟。样品的形貌与粒径采用扫描电镜来观测。电镜测试采用日本电子的JSM-5610LV型扫描电镜,放大5000-20000倍进行形貌观察。 The phase, structure and composition of the prepared hydroxyapatite/bagasse activated carbon were tested by a German Bruker-axs D8ADVANCE X-ray diffractometer, with a diffraction angle range of 2θ=10-90° and a diffraction rate of 4°/min . The morphology and particle size of the samples were observed by scanning electron microscopy. The electron microscope test adopts the JSM-5610LV scanning electron microscope of Japan Electronics, and the morphology is observed at a magnification of 5000-20000 times.
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