机构地区:[1]仲恺农业工程学院新型肥料研究中心/广东省农业产地环境污染防控工程技术研究中心
出 处:《植物营养与肥料学报》2019年第12期2061-2068,共8页Journal of Plant Nutrition and Fertilizers
基 金:国家自然科学基金项目(30971867,31172031);广东省农业资源环境共性关键技术创新团队建设任务(2019KJ118);广东省普通高校省级重大科研项目(自然科学)(粤教科函【2015】3号)(2014KZDXM058);广东省玉米产业技术体系创新团队建设任务(粤农农函【2019】1019号);广州市科技计划项目产学研协同创新重大专项(201704020187)
摘 要:【目的】电解质种类和浓度影响保水剂的吸水性能。探明保水剂与尿素、不同价态阳离子间的相互作用,对于正确使用和开发水肥调控性能优越的缓释材料具有重要意义。【方法】试验选用聚丙烯酰胺-丙烯酸盐型保水剂[P(AA-AM)]和聚丙烯酸盐型保水剂(PAA)。以分析纯盐酸盐和尿素分别配置了浓度1~256 mmol/L的尿素、NH4^+、Na^+、K^+、Mg^2+、Ca^2+、Fe^3+、Al^3+溶液。称取保水剂0.3000 g于75μm尼龙袋中,分别置于以上各系列溶液和去离子水300 mL中,静置12 h。取出保水剂袋,沥水30 min,以差减法测定保水剂吸水倍率和对溶质的吸附量。【结果】在溶质浓度从1 mmol/L增加到256 mmol/L时,尿素溶液中保水剂的吸水倍率没有显著下降,而各阳离子溶液中保水剂的吸水倍率显著下降,保水剂的相对吸水倍率与尿素、各种离子浓度之间呈显著幂函数的减函数关系,最终下降幅度由小到大依次为尿素、一价阳离子、二价阳离子、三价阳离子。保水剂对溶液中尿素和各种阳离子的吸附量随溶液浓度的增加而增加,P(AA-AM)的最大吸附量:尿素64.66 mmol/g、Na^+45.24 mmol/g、K^+34.26 mmol/g、NH4^+32.63 mmol/g、Mg^2+30.09 mmol/g、Ca^2+23.96 mmol/g、Fe^3+8.07 mmol/g、Al^3+12.74 mmol/g。保水剂对尿素和一、二价阳离子的吸附特征可用Freundlich等温吸附模型表征,对三价阳离子的吸附特征可用Langmuir等温吸附模型表征。尿素和二、三价阳离子对P(AA-AM)吸水倍率的影响均小于其对PAA的影响(P<0.05),一价阳离子对P(AA-AM)和PAA影响差异不明显(P>0.05)。P(AA-AM)吸附尿素和阳离子的能力要大于PAA(P<0.05)。【结论】保水剂对尿素的吸附量远高于阳离子,而尿素浓度基本不影响保水剂的保水性能。三价、二价和一价阳离子可显著降低保水剂的吸水倍率,阳离子浓度与保水剂的吸水倍率之间呈幂函数关系。保水剂对一价阳离子的最大吸附量大【Objectives】Water absorbing capacity of super absorbent polymer(SAP)is impacted by the type and concentration of co-existing electrolyte ions.Study of the interaction between SAP and urea or cations will help the correct choice of SAPs when use them in the coating materials of fertilizers.【Methods】Poly acrylateco-acrylamide[P(AA-AM)]and polyacrylate(PAA)were used as the tested SAPs in this study.1-256 mmol/L serious cation(urea)solutions were prepared using analytical purity grade urea,NH4Cl,NaCl,KCl,MgCl2,CaCl2,FeCl3 and AlCl3 individually.0.3000 g of the SPAs into nylon bags(75μm)were put into 300 mL of above solutions and deionized water and stood for 12 h.Then take the bags out of the solution and dried at air for 30 min.Difference subtraction methods were used to calculate the relative absorbance capacity to water and all the tested solutes.【Results】When the concentration of solute was increased from 1 to 256 mmol/L,the water absorbency of SAPs in urea solution was not decreased obviously,while in all the cation solutions decreased sharply.The relationship between the relative water absorbency of SAPs and the concentrations of cations could be fitted by power function.The decrease effects on water absorption capacity was in order of urea,monovalent catioans(NH4^+,Na^+,K^+)bivalent cations(Mg^2+,Ca^2+)and trivalent cations(Fe^3+,Al^3+).With the increase of solute concentration,the absorbed amount of solutes increased.The largest absorption of P(AA-AM)was urea 64.66 mmol/g,Na^+ 45.24 mmol/g,K^+ 34.26 mmol/g,NH4^+ 32.63 mmol/g,Mg2^+ 30.09 mmol/g,Ca^2+ 23.96 mmol/g,Fe^3+ 8.07 mmol/g and Al^3+ 12.74 mmol/g.The adsorption of SAPs to urea,monovalent and bivalent cations could be well described with Freundlich isotherm model,and that to trivalent cations with Langmuir isotherm model.The impaction of monovalent cations on the water absorbency of P(AA-AM)and PAA was not significantly different,while the impaction of divalent and trivalent cations on P(AA-AM)was less than that on PAA(P<0.05).The adsorption
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