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旱地小麦锌吸收转移与籽粒锌含量的关系OA北大核心CSTPCD

Relationships of grain zinc concentration with wheat zinc uptake and translocation in dryland

中文摘要英文摘要

[目的]黄土高原旱地小麦籽粒锌含量较低,明确土施锌肥引起的小麦花前花后锌吸收转移和籽粒锌含量的变化,及其与土壤锌形态及有效性关系,为优化旱地小麦锌营养强化技术提供科学依据.[方法]基于2017 年在黄土高原旱地石灰性土壤上开始的定位试验,于 2021-2022 和 2022-2023 年两个小麦生长季取样,研究锌肥用量对土壤有效锌及锌形态、小麦花前花后锌吸收转移及籽粒锌含量的影响.[结果]施用锌肥对小麦产量无显著影响,但两季小麦籽粒锌含量分别提高 44.7%和 38.2%,施锌 25.6 kg/hm2 时,籽粒锌含量最高达33.6 mg/kg,花前锌吸收量分别提高 38.8%~83.7%和 13.4%~49.0%,花后锌转移量分别提高 36.0%~73.9%和13.0%~39.6%;施锌对小麦花后锌吸收量的影响因年份而异.表层 0-20 和 20-40 cm土壤有效锌含量分别提高 11.6 和 11.3 倍,最高分别达 9.20 和 3.57 mg/kg,深层 40-60、60-80 和 80-100 cm土壤有效锌含量分别提高 4.4、1.8 和 1.9 倍,最高分别达 0.54、0.28 和 0.29 mg/kg.施用锌肥显著提高了土壤各形态锌含量,0-20 和20-40 cm土层水溶态锌分别提高 54.5%和 75.0%,达 0.17 和 0.14 mg/kg;松结有机态锌分别提高 214.9%和90.8%,达 5.70 和 3.11 mg/kg;碳酸盐结合态锌分别提高 1178.0%和 551.7%,达 5.24 和 1.89 mg/kg;氧化锰结合态锌分别提高 345.9%和 183.9%,达 15.52 和 9.37 mg/kg;紧结有机态锌分别提高 91.5%和 34.4%,达1.13和0.86 mg/kg;残渣态锌分别提高23.7%和24.3%,达56.57和56.80 mg/kg.[结论]施锌显著提高了土壤松结有机态、碳酸盐结合态和氧化锰结合态锌含量,并通过其向水溶态锌转化,维持了施锌后表层土壤有效锌提升和施入土壤的肥料锌的有效性,促进了小麦花前锌吸收,实现了花后地上部锌向籽粒的转移及籽粒锌含量提升,但干旱缺水影响了旱地小麦花后锌吸收,抑制了施锌后籽粒锌含量进一步提升.

[Objectives]Understanding the response of pre-and post-anthesis zinc(Zn)uptake and translocation in wheat to Zn fertilizer input and grain Zn concentration and their relationships with soil Zn fractions and its availability is of great importance to achieve grain Zn biofortification in drylands,particularly in the Loess Plateau where Zn is deficient in wheat grain.[Methods]Based on the location-fixed field experiment initiated in 2017 on dryland of the Loess Plateau,soil Zn fractions and availability,pre-and post-anthesis Zn uptake and transportation and grain Zn concentrations of wheat were analyzed under different Zn application rates in the cropping seasons of 2021-2022 and 2022-2023.[Results]Results showed that Zn application did not significantly affect grain yield,but grain Zn concentration was increased by 44.7%and 38.2%in two seasons,with the highest of 33.6 mg/kg at Zn 25.6 kg/hm2 application.Correspondingly,pre-anthesis Zn uptake was increased respectively by 38.8%-83.7%and 13.4%-49.0%in two seasons,post-anthesis Zn translocation was increased by 36.0%-73.9%and 13.0%-39.6%;while effects of Zn application on post-anthesis Zn uptake changed with years.Soil available Zn was increased by 11.6 and 11.3 times respectively in the top soil layers of 0-20 and 20-40 cm,with the highest available Zn concentrations of 9.20 and 3.57 mg/kg.Correspondingly,the increases of 4.4,1.8,and 1.9 times respectively in the deep soil of 40-60,60-80,and 80-100 cm,with the highest available Zn concentrations of 0.54,0.28,and 0.29 mg/kg.Zinc fractions also significantly changed with Zn application.Water-soluble Zn was increased by 54.5%and 75.0%and maximized to 0.17 and 0.14 mg/kg,Zn weakly bound to organic matter was increased by 214.9%and 90.8%and maximized to 5.70 and 3.11 mg/kg,carbonate bound Zn was increased by 1178.0%and 551.7%and maximized to 5.24 and 1.89 mg/kg,manganese oxide bound Zn was increased by 345.9%and 183.9%and maximized to 15.52 and 9.37 mg/kg,Zn strongly bound to organic matter was increased by 91.5%and 34.4%and maximized to 1.13 and 0.86 mg/kg,and residue mineral Zn was increased by 23.7%and 24.3%and maximized to 56.57 and 56.80 mg/kg in the soil layer of 0-20 and 20-40 cm,respectively.[Conclusions]Zn fertilizer application not only increased the concentration of Zn weakly bound to organic matter,carbonate bound Zn and manganese oxide bound Zn in soil but also promoted their transformation into a higher available fraction as water-soluble Zn,and this consequently could sustain the available Zn pool in top soil.The enhanced soil available Zn supply could increase wheat grain Zn concentration due to the promoted pre-anthesis Zn uptake and its transfer of Zn from shoot to grain post-anthesis,while the post-anthesis Zn uptake was inhibited by the inherent drought in dryland,the further grain Zn fortification with Zn fertilizer application was limited for wheat grown on the Loess Plateau.

丁玉兰;徐隽峰;罗一诺;李小涵;石美;王朝辉;黄翠;方佳创;李文虎;王星舒;张学美;党海燕;孙蕊卿;杨珺

西北农林科技大学资源环境学院/农业农村部西北植物营养与农业环境重点实验室,陕西杨凌 712100西北农林科技大学资源环境学院/农业农村部西北植物营养与农业环境重点实验室,陕西杨凌 712100||西北农林科技大学作物抗逆与高效生产全国重点实验室,陕西杨凌 712100

旱地小麦籽粒锌吸收转移土壤有效锌锌形态

drylandwheatgrain zinczinc uptake and translocationsoil available zinczinc fractions

《植物营养与肥料学报》 2024 (009)

1650-1664 / 15

国家现代农业产业技术体系建设专项(CARS-3).

10.11674/zwyf.2024098

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