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优化缓释氮肥与尿素配施比例提高冬小麦产量和氮肥利用效率

谷晓博, 宋慧, 白东萍, 杜娅丹, 常甜, 卢识宇, 蔡文璟

谷晓博,宋慧,白东萍,等. 优化缓释氮肥与尿素配施比例提高冬小麦产量和氮肥利用效率[J]. 农业工程学报,2023,39(11):56-65. DOI: 10.11975/j.issn.1002-6819.202212136
引用本文: 谷晓博,宋慧,白东萍,等. 优化缓释氮肥与尿素配施比例提高冬小麦产量和氮肥利用效率[J]. 农业工程学报,2023,39(11):56-65. DOI: 10.11975/j.issn.1002-6819.202212136
GU Xiaobo, SONG Hui, BAI Dongping, et al. Combined the application of slow-release N fertilizer and urea to improve the yield and N use efficiency of winter wheat[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2023, 39(11): 56-65. DOI: 10.11975/j.issn.1002-6819.202212136
Citation: GU Xiaobo, SONG Hui, BAI Dongping, et al. Combined the application of slow-release N fertilizer and urea to improve the yield and N use efficiency of winter wheat[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2023, 39(11): 56-65. DOI: 10.11975/j.issn.1002-6819.202212136

优化缓释氮肥与尿素配施比例提高冬小麦产量和氮肥利用效率

基金项目: 国家重点研发计划项目(2021YFD1900700)
详细信息
    作者简介:

    谷晓博,博士,教授,研究方向为农业节水理论与技术、农业水肥资源高效利用与调控。Email:guxiaobo@nwafu.edu.cn

  • 中图分类号: S512.1

Combined the application of slow-release N fertilizer and urea to improve the yield and N use efficiency of winter wheat

  • 摘要:

    为探究匹配冬小麦氮素需求规律的最佳缓释氮肥与尿素配施比例,优化施肥结构,达到氮肥高效利用与经济效益“双赢”的目标,该研究以冬小麦为研究对象,通过2 a(2019—2020年和2020—2021年)田间试验,设置7个施肥处理:仅施尿素(U)、仅施缓释氮肥(S)、缓释氮肥与尿素1:3配施(SU1)、缓释氮肥与尿素1:1配施(SU2)、缓释氮肥与尿素3:1配施(SU3)、不施氮肥(N0)和不施肥(CK),研究缓释氮肥配施比例对冬小麦干物质积累和转运、产量和氮肥利用效率的影响。结果表明,冬小麦干物质快速生长期和最大累积速率随缓释氮肥配施比例的增加而增加,缓释氮肥与尿素配施的冬小麦干物质平均累积速率比普通尿素提高1.90%~19.91%。缓释氮肥与尿素配施可在改善花前干物质转运量的同时提高花后生产量,花后干物质生产量对籽粒贡献率达53.18%~71.83%。产量随缓释氮肥配施比例的增加而显著提高,SU3处理2 a产量分别为7 243和8 021 kg/hm2,较S和U处理分别提高了7.25%和16.07%,其经济效益较S和U处理提高了15.18%和25.67%。与仅施尿素相比,缓释氮肥与尿素配施可显著提高氮肥利用效率,但SU2和SU3处理无显著差异(P>0.05)。综合考虑,在施氮量180 kg/hm2条件下,缓释氮肥与尿素配施比例50%(SU2),可实现冬小麦绿色高产高效,其产量为7 458 kg/hm2,氮肥吸收利用效率为45.97%,农学利用效率、生理利用效率和偏生产力分别为16.07、30.49和42.09 kg/kg。该研究可为冬小麦合理施肥提供理论依据。

    Abstract:

    Here, the best ratio of slow-release nitrogen fertilizer to urea was determined to match the nitrogen demand of winter wheat. The fertilizer application structure was also optimized for the efficient use of nitrogen fertilizer and economic benefits. Seven fertilizer treatments were applied into the winter wheat in a two-year field trial: urea only (U), slow-release N fertilizer only (S), slow-release N fertilizer with the urea 1:3 (SU1), 1:1 (SU2), and 3:1 (SU3), no N fertilizer (N0) and no fertilizer (CK). A systematic investigation was made to explore the effects of slow-release N fertilizer application rates on the dry matter accumulation and transport, yield, and N fertilizer use efficiency of winter wheat. The results showed that there was an increase in the rapid growth period and the maximum accumulation rate of dry matter in the winter wheat with the proportion of slow-release N fertilizer. The average dry matter accumulation rate of slow-release nitrogen fertilizer combined with the urea increased by 1.90% to 19.91%, compared with the ordinary urea. The proportion of slow-release nitrogen fertilizer application posed a significant impact on the post post-flowering dry matter production. There was an increase in the pre and post post-flowering dry matter transport. Meanwhile, the post post-flowering dry matter production was contributed 53.18% to 71.83% of the grain yield. The yield increased significantly with the increasing proportion of slow-release N fertilizer, with the two-year yields of 7 243 and 8 021 kg/hm2 in the SU3, which were 7.25% and 16.07% higher than the S and U treatments, respectively, and their economic benefits were 15.18% and 25.67%, respectively. The cumulative nitrogen uptake of winter wheat increased by the application of slow-release nitrogen fertilizer with the urea. Specifically, the cumulative nitrogen uptake values were 24.08% to 36.63% higher than those in the SU3, compared with the U treatment. The slow-release N fertilizer with the urea was improved the N fertilizer use efficiency. The agronomic use efficiency, physiological use efficiency, and biased productivity were improved in the SU3, compared with the U treatment. But there was no significant difference between SU2 and SU3 treatments (P>0.05). The slow-release N combined with the urea was significantly improved the N use efficiency, but there was no significant difference between SU2 and SU3 treatments (P>0.05). Therefore, the slow-release N fertilizer mixed with the urea can be expected to improve the winter wheat yield and N use efficiency. The dry matter growth period was significantly extended to promote the maximum accumulation rate for the post-flowering dry matter production and its transport rate to the seed. By comprehensive consideration, under the condition of nitrogen application rate of 180 kg/hm2, the combination of slow-release nitrogen fertilizer and urea application ratio of 50% (SU2) can achieve green, high yield, and high efficiency of winter wheat. Among them, the yield is 7 458 kg/hm2, the nitrogen fertilizer absorption and utilization rate is 45.97%, and the agronomic utilization rate, physiological utilization rate, and partial productivity are 16.07, 30.49, and 42.09 kg/kg, respectively. The finding can provide the theoretical basis for the rational fertilization of winter wheat. Follow-up studies need to consider the environmental effects and carbon and nitrogen emissions, together with the impact of slow-release nitrogen fertilizer combined with the urea on the soil nitrate nitrate-nitrogen distribution, ammonia volatilization, and greenhouse gas emissions. Further research can be conducted to determine the amount and proportion of slow-release nitrogen fertilizer and urea application for the high yield, high efficiency, and simultaneous emission reduction in winter wheat farmland.

  • 目前,许多传统薄膜材料的原料如聚乙烯(polyethylene,PE),聚氯乙烯(polyvinyl chloride, PVC),聚丙烯(polypropylene,PP)等石油基聚合物,由于其在土壤中极低的自然降解率,所堆积的残留物会破坏土壤结构,造成所谓的“白色污染”,并随着时间的推移通过生态系统的循环最终威胁到我们人类的健康[1-3]。针对这一现状,合理回收传统用膜及开发使用新型绿色生物可降解材料是当下控制和缓解的两种办法。但对于回收传统膜来说,由于较大的回收难度和较高的经济成本,阻碍了这一行动的实施[4]。因此,为了避免“白色污染”的进一步扩大,研制出具备传统石油基材料相同性能的绿色新型可生物降解材料是目前最优的方案。近年来,环境友好型材料得到了广泛关注和研究,其中的可生物降解材料能被微生物完全分解且不会对环境造成破坏,因此可以取代石油衍生物材料,解决环境污染问题。可生物降解材料,例如聚己内酯(polycaprolactone,PCL),聚乳酸(polylactic acid,PLA),聚乙烯醇(polyvinyl alcohol,PVA)等是常见的化工合成材料。其中,PVA由于其具备优异的生物安全性和可降解性以及较强的力学性能,使其成为了薄膜领域在内的众多领域的研究热点[5]。然而,由于PVA分子结构中含有的大量亲水性的羟基基团,使得PVA膜在潮湿环境下容易吸收空气中的水分而发生溶胀,进而影响膜的性能,限制了PVA在特定环境下的应用[6]。此外,PVA膜由于其不具备阻隔紫外线的能力,在用于特定包装材料及农业用膜时,紫外线的辐射作用会加速薄膜的老化,甚至直接危害到农作物的生长。因此,提升PVA薄膜的耐水性和光学性能是促进其广泛应用的必要条件。

    木质素(Lignin)是植物木质结构中三大主要成分之一,同时也是为数不多能够替代石油基多元醇提供芳香基化合物的可再生资源[7]。木质素主要是在化学制浆过程中作为一种废料产生的,但只有将近3.5%被用于生产高附加值产品[8]。因此探索木质素在高值化产品的应用对资源有效利用具有重要价值[9-10]。大量研究表明,木质素中含有大量的苯环,羰基和酚羟基,能够消除自由基使其具有一定的紫外吸收特性,同时赋予了生物相容性和可降解性等优点[11],且具备疏水基团如苯环,烷基链等。如ZHANG等 [12]将PVA与木质素进行共混后,木质素膜的机械性能和耐水性能都得到显著提升。IZAGUIRRE等[13]将木质素与壳聚糖(chitosan)进行共混后,共混膜的抗氧化性和阻隔紫外的能力得到了加强。因此,木质素的添加能够赋予和提高薄膜材料的性能。

    水性聚氨酯(waterborne polyurethane,WBPU)是一种将传统溶剂型聚氨酯换以H2O作为介质使聚氨酯分散在其中的新型聚氨酯体系,其不仅具有传统溶剂基聚氨酯优良的耐磨性和机械性能[14-15],在作为填料分散在其他组分体系中凭借着可调节性的软硬段使其赋予了材料新的柔韧特效[16],而且具有环保、安全可靠的特点使其在生物医药等方面大放异彩。

    因此,本文采取用微波法对木质素进行液化,将木质素液化物L(D)与PVA进行共混,并向体系中加入WBPU,制备L(D)/WBPU/PVA共混膜,对共混膜进行系统分析并探讨L(D)和WBPU对共混膜性能的影响。

    丙三醇、聚乙二醇-600(PEG-600)、木质素(脱碱)和水性聚氨酯(固含量为40%)均为分析纯,均由上海麦克林生化科技有限公司提供;浓硫酸(98%溶液)由广州化学试剂厂提供;聚乙烯醇1799型(醇解度98%~99%)由上海阿拉丁生化科技有限公司提供;无水乙醇(≥99.7%)购买于西陇科学股份有限公司。

    试验中主要使用的仪器设备:微波合成萃取仪,XM-MC-1,祥鹄科技有限公司;真空抽滤机,HQ-12CL-Ⅰ,祥鹄科技有限公司;旋转蒸发仪,Hei-VAP Advantage,Heidolph,德国;红外光谱仪,TENSOR27,Bruker,德国;X射线衍射仪,D8 ADVANCE,Brucker,德国;紫外分光光度计,UV-3300PC,MAPADA,中国上海;万能材料试验机,34SC-1,INSTRON,美国;台式扫描电镜,ProX,PHENOM,荷兰。

    将木质素放入120 ℃的烘箱进行脱水干燥处理120 min。之后,称取6 g木质素、24 g聚乙二醇-600(PEG-600)和6 g丙三醇放入圆底烧瓶中,在恒温磁力搅拌器上充分搅拌后,用移液枪吸取0.493 mL浓硫酸精准滴入混合试剂中以防止影响试验数据结果,继续搅拌一定时间后将烧瓶转移至微波合成萃取仪中 [17]。设置微波液化仪参数,仪器功率设置为600 W,反应时间设置在20 min,反应温度设置为160 ℃。待木质素液化结束后将其自然冷却至70 ℃,再将其进行真空抽滤,以除去残留固体,同时利用适量乙醇溶液把附着在烧瓶内的残留物冲洗后一并倒入漏斗中进行抽滤,待抽滤瓶中无液体滴漏后停止抽滤,将抽滤完成的混合液体移至旋蒸瓶中除去杂质乙醇。同时将抽滤后的滤纸放入60 ℃烘箱中干燥并进行后续称量。

    木质素的液化率计算可按照式(1)进行计算:

    W=W1W2W1×100 (1)

    式中,W为液化率,%;W1为木质素液化前的质量,g;W2为木质素未被液化的质量,g。

    分别称量干燥后的空白滤纸和带有未被液化的木质素的滤纸,得出的质量分别为0.31 g和1.06 g,根据公式(1)可得木质素的液化率约为87%,该结果较为明显的看出大部分木质素已被液化。

    本文采用溶液浇筑法来制备L(D)/WBPU/PVA共混膜。首先准确称量20 g PVA倒入单口烧瓶中并加入380 mL去离子水,再将其放入油浴锅中加热,加热温度为90 ℃,并在瓶口安装冷凝管,磁力搅拌约2 h后制得PVA质量分数为5%的澄清溶液,之后,停止加热,待溶液冷却至60 ℃时,按照表1的配比,向PVA溶液中分别加入不同含量L(D)的和WBPU,并在该温度下磁力搅拌2 h,直至共混液充分混合。随后,取65 mL共混溶液放入180 mm×130 mm的玻璃板上,在室温下铺平晾凉,期间做好除泡处理,每组重复4次,静置48 h后可得到完整的共混膜样品,其中所制样品的各种配比及其命名详见表1

    表  1  不同L(D)、WBPU添加量占比
    Table  1.  Different L (D) , WBPU addition %
    薄膜名称
    Film name
    L(D) WBPU
    PVA 0 0
    5%L(D)/PVA 5 0
    10%L(D)/PVA 10 0
    15%L(D)/PVA 15 0
    20%L(D)/PVA 20 0
    25%L(D)/PVA 25 0
    9:1 L(D)/WBPU/PVA 15 1.67
    8:2 L(D)/WBPU/PVA 15 3.75
    7:3 L(D)/WBPU/PVA 15 6.43
    6:4 L(D)/WBPU/PVA 15 10
    5:5 L(D)/WBPU/PVA 15 15
    注:L(D)为木质素液化物,PVA为聚乙烯醇,WBPU为水性聚氨酯,数字为L(D):WBPU掺比,实际添加量为占比×PVA质量,下同。
    Note:L(D) is lignin (Dealkaline) liquefaction, PVA is polyvinyl alcohol, WBPU is waterborne polyurethane, the data is the blending ratio of L(D):WBPU, the actual addition amount is proportion × PVA mass, same below.
    下载: 导出CSV 
    | 显示表格

    采用红外光谱仪记录PVA膜和共混膜的FTIR-ATR光谱,分辨率为4 cm−1,范围为4 000~600 cm−1,扫描16次。

    将膜的表平面和拉伸断截面用金溅射导电后,在10 kV下用Phenom ProX 扫描电镜观察。

    将薄膜裁成适当尺寸,采用紫外可见分光光度计测定在200~400 nm波长范围内共混膜的抗紫外性能和在400~800 nm波长范围内共混膜的不透明度和透光率。取完整均匀的共混膜,使用精度为0.001 mm的厚度测试仪在薄膜上随机取5个点,测定其厚度并计算平均值、标准差。依照式(2)计算特定波长下(600 nm)共混膜的不透明度[18]

    =AbsX×100% (2)

    式中,Abs为600 nm处共混膜的吸光度,X为共混膜的平均厚度,mm。

    使用配备45 kV和200 mA CuKα辐射的X射线衍射仪收集XRD光谱,并在8°~80°范围内以10(°)/min的扫描速率进行扫描。

    采用万能材料试验机测试薄膜的拉伸性能。将样品分别裁成三组尺寸为75 mm×4 mm的哑铃状薄膜以进行拉伸强度测试,测试夹具为间距50 mm,速度设为0.05 m/min,计算每个样品的平均值和标准偏差。

    从每张薄膜上割出2个尺寸为50 mm×50 mm的矩形薄膜。在60 ℃的真空烘箱中干燥24 h后,对样品的重量进行称量(W0),然后将其浸入100 mL去离子水中,浸没24 h后,使用滤纸去除样品表面多余的水,称量样品质量(Wt)。之后,放入60℃的烘箱中干燥24 h后,重新对此时的薄膜称量(Wd)。薄膜样品的吸水率(Wa)和水解率(Ws)使用以下公式测定[19]

    Wa=WtW0W0×100% (3)
    Ws=W0WdW0×100% (4)

    L(D)、WBPU、PVA能否以任意比例混合是证明三者具有良好相容性的有效依据。因此,对加入不同百分比液化物量的L(D)/PVA共混膜和掺杂了不同百分比含量WBPU的L(D)/WBPU/PVA共混膜都分别进行FTIR测试。结果如图1a所示,在纯PVA膜中,3 275 cm−1和2 939 cm−1的峰分别为-OH和-CH2的收缩振动,1 654 cm−1处的峰为-C=O的收缩振动,在1 420 cm−1处的峰为-C-H的平面振动,1 087 cm−1处的峰则是-C-O的收缩振动。在L(D)/PVA共混膜中,所有的样品均具有木质素液化物和PVA特征官能团的吸收峰,但其位置和峰形大小都有一定的改变。在1 420 cm−1附近的峰为次甲基的吸收峰,峰形随着L(D)的加入从尖变宽,强度相对变弱,这表明L(D)和PVA具有较强的氢键作用[20]。同时,随着L(D)含量不断增加,3 275 cm−1处的羟基峰总体上朝着高波数方向移动,在20%时为最大,这表明L(D)与PVA之间发生了相互作用。

    图  1  不同薄膜的红外光谱图
    Figure  1.  FTIR spectra of different films

    图1b为不同WBPU含量混膜的红外光谱图。3 368 cm−1附近宽峰为聚氨酯结构中的N-H和L(D)与PVA结构中羟基的吸收峰伸缩。1 731 cm−1附近则来自L(D)液化物与WBPU结构中-C=O的伸缩振动,且随着WBPU含量的增大,削弱了PVA中分子间的氢键作用,造成了PVA羟基峰逐渐蓝移[21-22]。同时由于固定含量PVA中的羟基数量不足,无法与WBPU中大量的羰基形成氢键,造成了能用于伸缩振动的羰基数目逐渐增多,对应的特征峰强度逐渐提高[23]。随着WBPU的不断加入,在1 087 cm−1附近属于PVA的-C-O伸缩振动强度呈现出从尖又强向着宽而弱变化,结晶度也随之衰弱。从以上结果表明,WBPU与L(D)/PVA具有较为不错的相容性。

    图2a可知,5%纯PVA膜的表面平整光滑,无明显颗粒,且拉伸断截面较为紧密、富有纹理。与纯PVA膜相比,L(D)/PVA膜表平面呈现出相似的特征,说明L(D)均匀分散在PVA基质中,形成了连续均匀相[24]。同时,随着木质素的不断加入,膜的拉伸断截面富有纹理且具有线条感,说明两者具有良好的生物相容性,膜的致密性好。但是随着木质素含量加到20%之后,膜的拉伸断截面的线条开始出现了一定程度上的紊乱,说明在分散过程中L(D)会出现一定程度的团聚现象,这可能会影响到膜的拉伸性能。

    图  2  薄膜的扫描电镜图
    注:a图中数值为L(D)质量分数,b图中数字为L(D):WBPU掺比,下同。
    Figure  2.  Scanning electron microscopy of the film
    Note: The figure in Fig. a is the L(D) mass fraction, and the figure in Fig. b is L (D) : WBPU blending ratio, same below.

    与2a图中的共混膜相比,随着WBPU含量的比例不断提高,图2b中L(D)/WBPU/PVA共混膜的断截面从有纹理愈发转变为粗糙状,在WBPU质量分数≥6.43%时尤为明显,且平面出现了较为明显的白色聚集体和复杂的结构交互,这在一定情况下会影响膜的综合性能。因此,WBPU的添加比例应该控制在6.43%以内,确保其能够均匀的分散在L(D)/PVA体系中[21,25]

    薄膜透明度是衡量透射光占入射光百分比强度的一项光学性能,也是评价薄膜材料性能好坏的特征[24]。从表2中可以清晰地观察到共混膜的厚度随着L(D)百分比的加入而逐渐提升,表明L(D)与PVA能够呈现稳定的相容,这与前面红外的分析基本吻合,且在可见光区的透明度较好。

    表  2  不同薄膜的厚度及不透明度
    Table  2.  Thickness and opacity of different films
    薄膜名称
    Film name
    厚度
    Thickness/mm
    吸光度Absorbance
    (600 nm)Abs
    不透明度
    Opaqueness/%
    PVA 0.115±0.007 0.0736 0.64±0.04
    5%L(D)/PVA 0.117±0.007 0.1344 1.15±0.07
    10%L(D)/PVA 0.127±0.019 0.2124 1.67±0.25
    15%L(D)/PVA 0.135±0.020 0.2421 1.79±0.27
    20%L(D)/PVA 0.142±0.014 0.2771 1.95±0.19
    25%L(D)/PVA 0.157±0.018 0.3010 1.92±0.22
    9:1 L(D)/WBPU/PVA 0.149±0.011 0.5392 3.61±0.28
    8:2 L(D)/WBPU/PVA 0.160±0.011 0.6493 4.06±0.27
    7:3 L(D)/WBPU/PVA 0.191±0.014 1.0047 5.26±0.38
    6:4 L(D)/WBPU/PVA 0.223±0.016 1.3836 6.21±0.46
    5:5 L(D)/WBPU/PVA 0.245±0.014 1.8714 7.63±0.45
    下载: 导出CSV 
    | 显示表格

    然而,WBPU的加入所呈现的现象则与其不同。在WBPU的比例小于3.75%时,共混膜的厚度也随着WBPU含量的增加而逐渐提升,但在超过3.75%后其厚度增加的幅度较大,这或许能进一步证实在WBPU质量分数时≥6.43%时,WBPU与L(D)/PVA基底存在着一定的相分离。所有的薄膜样品不透明度小于8,可以认为共混膜是透明的,如果应用于食品包装可以避免消费者对食品外观的误判。

    不同L(D)和WBPU含量的共混膜样品如图3所示,可以直观看出L(D)的加入使得共混膜呈现褐色,共混膜的颜色会随着L(D)含量的增加而加深,且WBPU的加入会加深L(D)中的褐色。

    图  3  制成的不同共混膜样品透光情况
    Figure  3.  Light transmission of different blended film samples

    紫外辐射对自然界动植物以及塑料制品造成一定程度影响,因此生产出能够较大程度在紫外光区吸收紫外光的产品具有很高的市场价值[26]。由图4共混膜紫外-可见光图谱可知,纯PVA膜在紫外区的吸收很小,例如在400 nm处时其透光率达到81.44%,而加入5%L(D)后共混膜的透光率降低至34.53%,这是由于PVA特殊的分子结构中不存在不饱和键,而恰好属于芳香族化合物的木质素,其骨架结构中的羰基以及不饱和共轭双键等能够对紫外线进行有效吸收[27],同时木质素中还具备特有的酚羟基,使其能够形成吸收紫外的共轭反应[28]。因此,共混膜吸收紫外的能力会随着L(D)的不断加入而增强,当L(D)含量为25%时,共混膜在400 nm处的透光率仅为1.64%,这能够说明L(D)能够明显改善共混膜的抗紫外性能。WBPU的加入同样使得共混膜的抗紫外能力得到了增强,在400 nm处,15%L(D)/PVA共混膜的透光率为7.69%,而加入了3.75%WBPU后,其光透过率降至1.57%,这可能是因为WBPU与L(D)形成了某种紫外光稳定体系,并随着WBPU含量的不断增加,400nm处的透光率接近于0。L(D)和WBPU的加入提升了共混膜的抗紫外性及抗老化性,这一特性可以应用于阻碍紫外线的包装薄膜和农业用膜[29]。但两者的加入都在某种程度上影响到了对可见光的透过率,这将在后续的研究中进行改善。

    图  4  不同薄膜的透过率测试
    Figure  4.  Transmittance test of different films

    图5a中可以看出纯PVA聚合物的特征衍射峰的分别出现在2θ=19.2°和26.3°。

    图  5  不同薄膜的XRD图谱
    Figure  5.  XRD patterns of different films

    当加入L(D)时,L(D)/PVA共混膜衍射图谱形状与纯PVA膜的无太大差异,说明L(D)均匀分散在PVA体系中。基于图5a的分析,图5b中L(D)/WBPU/PVA共混膜的XRD图谱中多出了一个2θ=22.6°的衍射峰,不难理解这属于WBPU硬段的结晶所导致的特征衍射信号峰[30]。当两者比例随着WBPU的不断增加,属于WBPU的衍射信号为缓慢增强,这可能是因为WBPU含量较低时,较高含量的L(D)会阻碍WBPU有序硬段间相互作用,但随着WBPU含量较高时,固定含量的L(D)反而促进了与WBPU链段间的相互作用,促使无规则软段部分结晶化,有序硬段部分增强[31]。同时在2θ=26.3°所展现的特征信号峰的强度也随之逐渐变弱,原因在于WBPU的加入能够一定程度的削弱L(D)/PVA分子间的强相互作用力,从而间接导致了共混膜的结晶度降低。

    拉伸性能好坏是衡量薄膜抗拉扯能力和断裂程度的重要参考标准,同时也是力学表征试验的基础因素。图6展示了两种共混膜的力学拉伸性能。

    图  6  不同薄膜的力学拉伸性能
    Figure  6.  Mechanical tensile properties of different films

    图6a可知,随着L(D)含量的不断加入,L(D)/PVA共混膜的拉伸性能呈现的变化趋势为先升后降,且当加入到15%的L(D)时,共混膜的拉伸强度达到顶峰(46.23 MPa),与纯PVA膜的拉伸强度(42.07 MPa)相比提升了10.60%。这是由于低含量的L(D)加入,其特有的空间网络结构与PVA混合发生相互作用后,导致共混膜形成了一种刚性结构,同时两者之间还能够形成分子间氢键,从而提升了拉伸性能[32]。继续提高L(D)比例至20%~25%时强度则有所下降,其原因可能是共混膜中过多的L(D)无法与PVA基体很好的结合,削弱了两者之间的相互作用,同时L(D)形成了一定程度的堆积[24],最终造成了膜拉伸强度的下降。断裂伸长率也呈现出相同的趋势。

    与上述分析的情况不同,图6b所展示的共混膜相对于未加入WBPU的共混膜来说整体的拉伸强度下降幅度很大,且随着WBPU的不断加入,拉伸强度也呈现下降趋势,这是因为WBPU中某些链段能够代替L(D)和PVA分子间和分子内氢键作用与L(D)和PVA分子间氢键进行相互作用,削弱了L(D)和PVA分子间的作用力[33-34]。同时L(D)/WBPU/PVA共混膜的断裂伸长率与未添加WBPU的L(D)/PVA共混膜相比,均低于后者,且随着WBPU的不断增加,断裂伸长率也随之降低,直至WBPU的添加量≥10%时才开始回升。分析认为,是由于引入的L(D)使得WBPU中硬段含量上升,分子之间的交联度增强,降低了共混膜随拉伸强度变化而发生形变的能力,导致膜的脆性变大,断裂伸长率下降[34-35]。后来的回升则是由于共混膜中的L(D)不足以充当过多的WBPU硬段。

    图7a展示了L(D)的含量对共混膜吸水性和水溶性的影响规律。

    图  7  不同薄膜的吸水性和水溶性结果
    Figure  7.  Water absorption and water solubility results of different films

    PVA是强亲水性材料容易吸水膨胀,但随着L(D)的加入其吸水性逐渐降低,当加入15%的L(D)时,共混膜的吸水率从532%降低至362%,其耐水性提升了32%,这是因为L(D)进行液化后,部分羟基被酯化不与羰基产生共轭效应,与水形成氢键的能力变小,同时液化后的产物还有酚羟基,导致疏水性能的增加[36]。而水溶性的变化走势较为复杂,呈现出微弱的降-升-降的变化。相比于纯PVA膜,加入5%L(D)的共混膜其水溶性从42%下降至35%,但当L(D)含量高于5%时,膜的水溶性在35%附近波动。造成这一现象的原因可能是由于L(D)疏水性造成的,同时还与L(D)本身复杂的刚性分子结构有这一定联系[37]

    而加入WBPU的水溶性则没有这种复杂变化。由图7b可知,L(D)/WBPU/PVA共混膜与L(D)/PVA共混膜对比整体的吸水性和水溶性都明显降低。随着WBPU的不断加入,吸水性为降低的走势,其中5:5L(D)/WBPU/PVA共混膜的吸水率甚至降至170%,水溶性也降至18%,耐水性相较于纯PVA膜来说提升了68%。这是因为WBPU吸水性低且具有很强的尺寸稳定性,交联作用下削弱了PVA中大量的羟基氢键的形成[24];而水溶性也呈现出不断下降的趋势,同样是因为在整个共混膜中体系中PVA的占比随着WBPU的不断加入而越来越小,使得降低了共混膜的亲水性能,水分子由膜的内层逐渐向表面扩散[38]

    1)一定含量L(D)的加入在一定程度上能够提升L(D)/PVA共混膜的拉伸强度,且在L(D)含量为15%时拉伸强度从42.07 MPa增加到46.53 MPa,提高了10.60%;并且L(D)的加入能够显著的改善共混膜吸收紫外光辐射的能力,且透明度较好。同时L(D)的加入改善了共混膜整体的耐水性。综合考虑,L(D)加入量为15%时,共混膜整体性能最佳。

    2)在WBPU的加入下,L(D)/WBPU/PVA共混膜整体的抗紫外能力和耐水性都得到进一步的增强。但是在力学性能上,由于WBPU能够削弱L(D)和 PVA分子间作用力,拉伸强度上则有一定程度的下降。因此,综合考虑下7:3比例下的共混膜性能最佳。

    3)在该试验研究和过程分析中,经过液化后的L(D)和WBPU都对PVA膜的性能产生了一定影响,尤其是在抗紫外性能和耐水性能上表现出了优异的提升效果。L(D)/WBPU/PVA共混膜可用作良好的紫外屏蔽材料和防水材料,可应用于特殊包装和地膜等,同时为L(D)/WBPU/PVA共混膜制备的合理性提供了理论依据,并对其在农用膜的应用有一定的参考意义。

  • 图  1   2019—2021年冬小麦生育期内日平均气温和日降水量

    Figure  1.   Daily air temperature and precipitation during the growth period of winter wheat in 2019—2021

    图  2   硫包衣尿素(SCU)的缓释曲线

    Figure  2.   Slow-release curves for sulfur-coated urea (SCU)

    图  3   2019—2021年冬小麦生育期内干物质动态累积过程

    Figure  3.   Dynamic accumulation process of dry matter (DM) in winter wheat growth period from 2019 to 2021

    图  4   2019—2021年冬小麦花后生产量与产量之间的拟合关系

    Figure  4.   The fitting relationship between translocation after flowering and yield of winter wheat from 2019 to 2021

    图  5   2019—2021年不同处理下冬小麦地上部氮素累积量

    Figure  5.   Nitrogen uptake accumulation of winter wheat under different treatments from 2019 to 2021

    图  6   2019—2021年不同处理对冬小麦氮素利用效率的影响

    Figure  6.   Effects of different treatments on nitrogen use efficiency of winter wheat from 2019 to 2021

    表  1   各处理设计

    Table  1   Design of different treatments

    处理
    Treatment
    缓释氮肥与
    尿素比例
    Ratio of slow-
    release N
    fertilizer to urea
    施肥量Fertilizer application rate/(kg·hm−2)
    普通氮肥
    Common
    N fertilizer
    缓释氮肥
    Slow-release
    N fertilizer
    磷肥
    Phosphorus
    fertilizer
    钾肥
    Potassium
    fertilizer
    CK
    N000120135
    U180120135
    S180120135
    SU11:313545120135
    SU21:19090120135
    SU33:145135120135
    注:试验所用普通氮肥为尿素(N≥46%),缓释氮肥为硫包衣尿素(N≥37%),磷肥为过磷酸钙(P2O5≥16%),钾肥为硫酸钾(K2O≥51%)。
    Note: The common nitrogen fertilizer used in the experiment is urea(N≥46%), slow-release nitrogen fertilizer is sulfur coated urea (N≥37%), phosphorus fertilizer is superphosphate (P2O5≥16%), and potassium fertilizer is potassium sulfate (K2O≥51%).
    下载: 导出CSV

    表  2   不同处理下冬小麦地上部干物质动态Logistic方程拟合参数

    Table  2   Fitted parameters of Logistic equations for aboveground dry matter dynamics of winter wheat under different treatments

    年份Year处理TreatmentYmax/(kg·hm−2)R2T1/dT2/dT/dVmean/(kg·hm−2·d−1)Vmax/(kg·hm−2·d−1)Tmax/d
    2019—2020CK81880.98916119837133146179
    N098080.99016119736162178179
    U138130.99216219533216237179
    S141170.99016319835244269181
    SU1147790.99116219634261287179
    SU2151920.99416019535258283178
    SU3153880.99415919536259285177
    2020—2021CK44840.958177202257886184
    N079110.98217820628170186192
    U118420.98417820527263289192
    S123820.98917520631242266190
    SU1130620.99017420531252276189
    SU2138560.98917420632258284190
    SU3149450.98617520833268295191
    注:Ymax,最大干物质累积量;T1T2,干物质快速累积起始时间和结束时间;T,干物质快速生长期;Vmean,干物质平均累积速率;Vmax,干物质最大累积速率;Tmax,达到干物质最大累积速率的时间。
    Note: Ymax, maximum accumulated dry matter; T1 and T2, initial and end time of rapid dry matter accumulation; T, rapid growth period of dry matter; Vmean, average dry matter accumulation rate; Vmax, maximum accumulation rate of dry matter; Tmax, time to reach the maximum dry matter accumulation rate.
    下载: 导出CSV

    表  3   2019—2021年不同处理下冬小麦营养器官的花前贮藏干物质转运量与花后干物质生产量

    Table  3   Storage dry matter transportation before flowering and photochemical production after flowering in winter wheat under different treatments from 2019 to 2021

    年份
    Year
    处理
    Treatment
    花前Before flowering花后After flowering
    转运量
    Translocation/(kg·hm−2)
    贡献率
    Contribution/%
    生产量
    Translocation/(kg·hm−2)
    贡献率
    Contribution/%
    2019—2020CK1 959±19 d44.93a2 401±70e55.07 d
    N01 765±40e30.23cd4 074±81c69.77ab
    U2 615±70b39.96b3 929±120c60.04c
    S2 930±85a43.28a3 840±99 d56.72 d
    SU12 257±7c31.95c4 809±41b68.05b
    SU22 277±1c31.70c4 904±27b68.30b
    SU32 040±60 d28.17 d5 203±56a71.83a
    2020—2021CK1 115±30c46.82ab1 227±30 d53.18ab
    N01 952±70bc55.16a1 576±66 d44.84b
    U2 871±22ab46.38ab3 314±75c53.62ab
    S2 830±47ab42.85b3 750±67bc57.15a
    SU13 200±42a40.72b4 724±48abc59.28a
    SU23 034±76a38.08b4 936±89ab61.92a
    SU33 089±89a35.99b5 515±82a64.01a
    显著性检验F值Significance test F value
    配施比例Proportion of application(PA)0.5131.94**7.53**31.94**
    年份Year (YR)15.77**52.42**0.1352.42**
    PA×YR2.225.92**0.665.92**
    注:不同小写字母表示相同年份不同处理间差异显著(P<0.05)。*,P<0.05;**,P<0.01。下同。
    Note: Different lowercase letter indicates significant differences among treatments in the same year (P<0.05). *, P<0.05; **, P<0.01. Same as below.
    下载: 导出CSV

    表  4   2019—2021年不同处理冬小麦产量及其构成因素

    Table  4   Grain yield and yield components of winter wheat under different treatments from 2019 to 2021

    年份
    Year
    处理
    Treatment
    穗数
    Ear number
    穗粒数
    Grain number per spike
    穗长
    Ear length/cm
    千粒质量
    1000-grain weight/g
    产量
    Yield/(kg·hm−2)
    2019—2020CK338±10 d34±1c5.1±0.2 c26.6±0.7 e4 360±115 f
    N0405±11 c33±1c5.2±0.3 c28.9±0.5 d5 839±85 e
    U524±13 b39±2 b5.8±0.3 b34.8±0.8 c6 543±54 d
    S546±15 b42±1 ab6.3±0.2 a36.4±0.7 b6 770±79 c
    SU1563±10 b44±2 a6.2±0.1 a40.9±0.3 a7 066±48 b
    SU2631±16 a43±1 ab6.5±0.1 a41.7±0.3 a7 180±26 ab
    SU3641±17 a44±2 a6.6±0.3 a41.8±0.2 a7 243±49 a
    2020—2021CK217±8 c29±1 c9.6±0.3 c44.2±1.1 a2 955±88 d
    N0214±6 c37±1 b9.6±0.3 c39.9±1.2 b3 378±100 d
    U301±8 b57±2 a10.5±0.3 b36.4±1.1 c6 605±80 c
    S327±10 b57±1 a12.0±0.2 a38.0±0.9 bc7 461±75 ab
    SU1314±10 b57±2 a11.0±0.3 b39.1±1.1 bc7 365±53 b
    SU2335±11 b55±2 a11.1±0.3 b39.4±1.1 bc7 736±79 ab
    SU3384±12 a51±2 a11.0±0.2 b38.7±0.8 bc8 021±64 a
    显著性检验F值Significance test F value
    PA16.45**0.926.93**25.16**4.92**
    YR800.14**150.24**1687.53**4.198.59**
    PA×YR2.753.04*3.46*6.58**0.65
    下载: 导出CSV

    表  5   2019—2021年不同处理冬小麦的经济效益

    Table  5   Economic benefits of winter wheat under different treatments from 2019 to 2021 元·hm−2

    年份
    Year
    处理
    Treatment
    产值
    Income
    投入Outcome总投入
    Total outcome
    净效益
    Economic benefit
    种子Seed肥料Fertilizer种植Cultivation收获Harvest其他Other
    2019—2020CK6 540 f75009757501 5003 9752 565 d
    N08 759 e7505259757501 5004 5004 259 c
    U9 816 d7507959757501 5004 7705 046 b
    S10 156 c7501 1379757501 5005 1125 044 b
    SU110 599 b7508819757501 5004 8565 744 a
    SU210 771 ab7509669757501 5004 9415 830 a
    SU310 865 a7501 0529757501 5005 0275 838 a
    2020—2021CK4 610 c73101 0287501 5004 009601 c
    N05 270 c7315131 0287501 5004 522748 c
    U10 305 b7317831 0287501 5004 7925 513 b
    S11 640 ab7311 1071 0287501 5005 1166 524 ab
    SU111 491 ab7318641 0287501 5004 8736 617 ab
    SU212 069 a7319451 0287501 5004 9547 115 a
    SU312 513 a7311 0261 0287501 5005 0357 478 a
    下载: 导出CSV
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出版历程
  • 收稿日期:  2022-12-17
  • 修回日期:  2023-04-03
  • 网络出版日期:  2023-08-01
  • 刊出日期:  2023-06-14

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