土壤初始有效磷和交换性镁含量改变了小麦生长对pH的响应

doi:10.13304/j.nykjdb.2022.0496

中国农业科技导报 ›› 2023, Vol. 25 ›› Issue (11): 173-181.DOI: 10.13304/j.nykjdb.2022.0496

• 生物制造资源生态 • 上一篇

土壤初始有效磷和交换性镁含量改变了小麦生长对pH的响应

张璐¹(), 郑磊², 刘思汝³, 蔡泽江¹(), 孙楠¹, 张强²(), 徐明岗¹^,³

^1.中国农业科学院农业资源与农业区划研究所，农业农村部耕地质量监测与评价重点实验室，北京 100081
^2.金正大生态工程集团股份有限公司，山东临沭 276700
^3.中国热带农业科学院南亚热带作物研究所，海南省热带作物营养重点实验室，广东湛江 524091

收稿日期:2022-06-04 接受日期:2022-08-29 出版日期:2023-11-15 发布日期:2023-11-20
通讯作者: 蔡泽江,张强
作者简介:张璐E-mail：zhanglu01@caas.cn
基金资助:
泰山产业领军人才工程项目(LJNY201818);海南省热带作物营养重点实验室开放课题项目(21KLTCN01)

Soil Initial Available Phosphorus and Exchangeable Magnesium Shaping the Response of Wheat Growth to pH

Lu ZHANG¹(), Lei ZHENG², Siru LIU³, Zejiang CAI¹(), Nan SUN¹, Qiang ZHANG²(), Minggang XU¹^,³

^1.Key Laboratory of Arable Land Quality Monitoring and Evaluation of Ministry of Agriculture and Rural Affairs，Institute of Agricultural Resources and Regional Planning，Chinese Academy of Agricultural Sciences，Beijing 100081，China
^2.Kingenta Ecological Engineering Group Co. ，Ltd. ，Shandong Linshu 276700，China
^3.Key Laboratory of Tropical Crops Nutrition of Hainan Province，South Subtropical Crops Research Institute，Chinese Academy of Tropical Agricultural Sciences，Guangdong Zhanjiang 524091，China

Received:2022-06-04 Accepted:2022-08-29 Online:2023-11-15 Published:2023-11-20
Contact: Zejiang CAI,Qiang ZHANG

摘要/Abstract

摘要：

酸害阈值作为土壤酸度改良的目标pH，对农业生产和可持续发展具有重要指导意义。通过盆栽试验，分析了5种不同母质土壤上小麦生长对pH的响应及其与土壤初始性质的关系。结果表明，板页岩、第四纪红土、河流冲积物、红砂岩和花岗岩发育的红壤上小麦地上部生物量稳定值分别为2.71、1.17、2.06、1.57和1.70 g·pot^-1；达到稳定值95%、50%和5%时的pH阈值（即pH_95%、pH_50%、pH_5%），板页岩发育的红壤分别为5.31、4.42和3.53，第四纪红土发育的红壤分别为5.79、4.79和3.80，河流冲积物发育的红壤分别为5.25、4.71和4.16，红砂岩发育的红壤分别为4.94、4.61和4.29，花岗岩发育的红壤分别为5.72、4.66和3.59。小麦地上部生物量稳定值与土壤初始pH、有效磷、交换性镁和交换性钙含量呈显著或极显著正相关，pH_50%与有效磷含量呈显著负相关；株高pH_50%与土壤初始有效磷含量、交换性镁含量呈显著负相关。结果表明作物酸害阈值受土壤初始有效磷和交换性镁含量的影响，土壤肥力水平和酸度共同决定了作物的最大生物量，为培肥土壤、降低酸害影响提供了科学依据。

关键词: 不同母质土壤, 酸害阈值, 有效磷, 交换性镁, pH

Abstract:

The critical pH was the target pH for soil acidity improvement， which has important guiding significance for agricultural production and sustainable development. A pot experiment was conducted to investigate the effect of soil initial properties affecting the response of wheat growth to pH. 5 soils derived from plate shale， quaternary red earth， river alluvium， tertiary red sandstone， and granite were used in this study. The results showed that the maximum shoot biomasses of wheat were 2.71， 1.17， 2.06， 1.57 and 1.70 g·pot^-1 for soils derived from plate shale， quaternary red earth， river alluvium， granite， and tertiary red sandstone， respectively. The critical values of pH_95%， pH_50%， or pH_5% were defined as shoot biomass reaching to 95%， 50%， or 5% of maximum values. The pH_95%， pH_50%， or pH_5% were 5.31， 4.42， and 3.53 for soil derived from plate shale， 5.79， 4.79， and 3.80 for quaternary red earth， 5.25， 4.71， and 4.16 for river alluvium， 4.94， 4.61， and 4.29 for tertiary red sandstone granite， and 5.72， 4.66， and 3.59 for granite， respectively. The maximum values of shoot biomass had significant positive correlations with soil initial pH， available P， exchangeable Mg and exchangeable Ca. The pH_50% of wheat shoot biomass was negatively correlated with soil initial available P； and the pH_50% of wheat height was negatively correlated with soil initial available P and exchangeable Mg. The data indicated that soil initial available P and exchangeable Mg shaped the response of wheat growth to pH and the maximum values of crop biomass were determined by both soil nutrient status and acidity. Therefore， we recommend that co-amelioration of soil fertility and acidity was a practical method to reach a best condition for plant growth.

Key words: soil parent materials, critical values, available P, exchangeable Mg, pH

中图分类号:

S156

张璐, 郑磊, 刘思汝, 蔡泽江, 孙楠, 张强, 徐明岗. 土壤初始有效磷和交换性镁含量改变了小麦生长对pH的响应[J]. 中国农业科技导报, 2023, 25(11): 173-181.

Lu ZHANG, Lei ZHENG, Siru LIU, Zejiang CAI, Nan SUN, Qiang ZHANG, Minggang XU. Soil Initial Available Phosphorus and Exchangeable Magnesium Shaping the Response of Wheat Growth to pH[J]. Journal of Agricultural Science and Technology, 2023, 25(11): 173-181.

图/表 9

参考文献 21

1	徐明岗, 文石林, 周世伟, 等. 南方地区红壤酸化及综合防治技术[J]. 科技创新与品牌, 2016 (7): 74-77.
	XU M G, WEN S L, ZHOU S W, et al.. Acidification and integrated control techniques of red soil in southern China [J]. Sci. Technol. Innov., 2016(7): 74-77.
2	GUO J H, LIU X J, ZHANG Y, et al.. Significant acidification in major Chinese croplands [J]. Science, 2010, 327(5968): 1008-1010.
3	徐仁扣. 土壤酸化及其调控研究进展[J]. 土壤, 2015, 47(2): 238-244.
	XU R K. Research progresses in soil acidification and its control [J]. Soils, 2015, 47(2): 238-244.
4	CAI Z J, WANG B R, XU M G, et al.. Intensified soil acidification from chemical N fertilization and prevention by manure in an 18-year field experiment in the red soil of southern China [J]. J. Soil Sediment., 2015, 15(2): 260-270.
5	MULLEN C L, SCOTT B J, EVANS C M, et al.. Effect of soil acidity and liming on lucerne and following crops in central-western New South Wales [J]. Anim. Prod. Sci., 2006, 46(10): 1291-1300.
6	蔡泽江, 孙楠, 王伯仁, 等. 长期施肥对红壤 pH、作物产量及氮、磷、钾养分吸收的影响[J]. 植物营养与肥料学报, 2011, 17(1): 71-78.
	CAI Z J, SUN N, WANG B R, et al.. Effects of long-term fertilization on pH of red soil crop yields and uptakes of nitrogen, phosphorous and potassium [J]. J. Plant Nutr. Fert., 2011, 17(1): 71-78.
7	ZHU Q C, LIU X J, HAO T X, et al.. Cropland acidification increases risk of yield losses and food insecurity in China [J/OL]. Environ. Pollut., 2020, 256: 113145 [2022-05-12]. .
8	BAQUY M A, LI J Y, JIANG J, et al.. Critical pH and exchangeable Al of four acidic soils derived from different parent materials for maize crops [J]. J. Soil Sediment., 2018, 18:1490-1499.
9	梁文君, 蔡泽江, 宋芳芳, 等. 不同母质发育红壤上玉米生长与土壤pH、交换性铝、交换性钙的关系[J]. 农业环境科学学报, 2017, 36(8): 1544-1550.
	LIANG W J, CAI Z J, SONG F F, et al.. Relationships between maize growth and the pH, exchangeable aluminum and calcium of red soils derived from different parent materials [J]. J. Agro-Environ. Sci., 2017, 36(8): 1544-1550.
10	BACHE B W, CROOKE W M. Interactions between aluminum, phosphorus and pH in the response of barley to soil acidity [J]. Plant Soil, 1981, 61(3): 365-375.
11	成杰民, 胡光鲁, 潘根兴, 等. 用酸碱滴定曲线拟合参数表征土壤对酸缓冲能力的新方法[J]. 农业环境科学学报, 2004, 23 (3): 569-573.
	CHENG J M, HU G L, PAN G X, et al.. New method for evaluating buffering capacity and equilibrium pH of paddy soil with simulation parameter [J]. J. Agro-Environ. Sci., 2004, 23(3): 569-573.
12	汪吉东, 冯冰, 李传哲, 等. 中国几种典型土壤酸碱缓冲容量测定方法的比较[J]. 江苏农业学报, 2020, 36(6): 1452-1458.
	WANG J D, FENG B, LI C Z, et al.. Comparative study on determination methods for acid buffering capacity of several typical soils in China [J]. Jiangsu J. Agric. Sci., 2020, 36(6): 1452-1458.
13	鲍士旦. 土壤农化分析[M]. 北京: 中国农业出版社, 2000:1-495.
14	王如月, 袁世力, 文武武, 等. 磷对铝胁迫紫花苜蓿幼苗根系生长和生理特征的影响[J]. 草业学报, 2021, 30(10): 53-62.
	WANG R Y, YUAN S L, WEN W W, et al.. Effects of phosphorus on root growth and photosynthetic physiology of alfalfa seedlings under aluminum stress [J]. Acta Pratac. Sin., 2021, 30(10): 53-62.
15	艾佐佐, 袁军, 黄丽媛, 等. 磷对铝胁迫下油茶幼苗根冠比及根系形态的影响[J]. 江苏农业科学, 2017, 45(12): 106-108.
	AI Z Z, YUAN J, HUANG L Y, et al.. Effects of phosphorus on root-shoot ratio and root morphology of camellia oleifera seedlings under aluminum stress [J]. Jiangsu Agric. Sci., 2017, 45(12): 106-108.
16	朱美红, 蔡妙珍, 吴韶辉, 等. 磷对铝胁迫下荞麦元素吸收与运输的影响[J]. 水土保持学报, 2009, 23(2): 183-187.
	ZHU M H, CAI M Z, WU S H, et al.. Effect of phosphorus on element uptake and transportation in buckwheat under aluminum stress [J]. J. Soil Water Conserv., 2009, 23(2): 183-187.
17	王宁, 郑怡, 王芳妹, 等. 铝毒胁迫下磷对荞麦根系铝形态和分布的影响[J]. 水土保持学报, 2011, 25(5): 168-171.
	WANG N, ZHENG Y, WANG F M, et al.. Effect of phosphorus on speciation and distribution of aluminum in the roots of buckwheat under aluminum toxicity [J]. J. Soil Water Conserv., 2011, 25(5): 168-171.
18	吴良泉. 科学施镁, 让土地“美”起来! [J]. 中国农资, 2018 (46): 24.
	WU L Q. Let the land “beautiful” up by scientific applying magnesium [J]. China Agri-product. News, 2018(46): 24.
19	赵越, 杨金玲, 许哲, 等. 模拟酸雨淋溶下不同母质发育雏形土矿物风化中的盐基离子与硅计量关系[J/OL]. 土壤学报, 2022 [2022-05-12]. .
	ZHAO Y, YANG J L, XU Z, et al.. Stoichiometry of base cations and silicon of cambosols derived from different parent materials as leached by simulated acid rain [J/OL]. Acta Pedol. Sin., 2022 [2022-05-12]. .
20	BOSSOLANI J W, CRUSCIOL C A C, MORETTI L G, et al.. Improving soil fertility with lime and phosphogypsum enhances soybean yield and physiological characteristics [J/OL]. Agron. Sustain. Dev., 2022, 42: 26 [2022-05-12]..
21	LAURICELLA D, BUTTERLY C R, CLARK G J, et al.. Effectiveness of innovative organic amendments in acid soils depends on their ability to supply P and alleviate Al and Mn toxicity in plants [J]. J. Soil Sediment., 2020, 20(11): 3951-3962.

土壤母质 Soil parent material	pH	有机质 Organic matter/（g·kg^-1）	碱解氮 Available nitrogen/（mg·kg^-1）	有效磷 Available phosphorus/（mg·kg^-1）	有效钾 Available potassium/（mg·kg^-1）	交换性氢 Exchangeable hydrogen/（cmol₊·kg^-1）	交换性铝 Exchangeable aluminum/（cmol₊·kg^-1）	交换性镁 Exchangeable magnesium/（cmol₊·kg^-1）	交换性钙 Exchangeable calcium/（cmol₊·kg^-1）
板页岩 Plate shale	5.93	23.3	120.1	30.4	81.3	0.07	0.07	1.35	6.80
第四纪红土 Quaternary red earth	4.60	16.1	76.7	5.7	87.5	0.72	4.61	0.26	1.52
河流冲积物 River alluvium	5.39	17.8	105.9	15.4	50.0	0.25	0.62	0.52	3.73
红砂岩 Tertiary red sandstone	4.45	30.6	175.4	9.7	68.8	0.24	7.76	0.23	0.72
花岗岩 Granite	4.74	39.4	217.7	12.1	62.5	0.19	4.34	0.15	0.37

土壤母质 Soil parent material	pH	有机质 Organic matter/（g·kg^-1）	碱解氮 Available nitrogen/（mg·kg^-1）	有效磷 Available phosphorus/（mg·kg^-1）	有效钾 Available potassium/（mg·kg^-1）	交换性氢 Exchangeable hydrogen/（cmol₊·kg^-1）	交换性铝 Exchangeable aluminum/（cmol₊·kg^-1）	交换性镁 Exchangeable magnesium/（cmol₊·kg^-1）	交换性钙 Exchangeable calcium/（cmol₊·kg^-1）
板页岩 Plate shale	5.93	23.3	120.1	30.4	81.3	0.07	0.07	1.35	6.80
第四纪红土 Quaternary red earth	4.60	16.1	76.7	5.7	87.5	0.72	4.61	0.26	1.52
河流冲积物 River alluvium	5.39	17.8	105.9	15.4	50.0	0.25	0.62	0.52	3.73
红砂岩 Tertiary red sandstone	4.45	30.6	175.4	9.7	68.8	0.24	7.76	0.23	0.72
花岗岩 Granite	4.74	39.4	217.7	12.1	62.5	0.19	4.34	0.15	0.37

土壤母质 Soil parent material	稳定值 Stable value/（g·pot^-1）	阈值Critical value
土壤母质 Soil parent material	稳定值 Stable value/（g·pot^-1）	pH_95%	pH_50%	pH_5%
板页岩 Plate shale	0.59	6.20	4.79	3.39
第四纪红土 Quaternary red earth	0.41	4.73	4.40	4.07
河流冲积物 River alluvium	0.49	5.60	4.91	4.21
红砂岩 Tertiary red sandstone	0.40	4.70	4.28	3.87
花岗岩 Granite	0.48	4.38	4.27	4.16

土壤母质 Soil parent material	稳定值 Stable value/（g·pot^-1）	阈值Critical value
土壤母质 Soil parent material	稳定值 Stable value/（g·pot^-1）	pH_95%	pH_50%	pH_5%
板页岩 Plate shale	0.59	6.20	4.79	3.39
第四纪红土 Quaternary red earth	0.41	4.73	4.40	4.07
河流冲积物 River alluvium	0.49	5.60	4.91	4.21
红砂岩 Tertiary red sandstone	0.40	4.70	4.28	3.87
花岗岩 Granite	0.48	4.38	4.27	4.16

土壤母质 Soil parent material	稳定值 Stable value/cm	阈值Critical value
土壤母质 Soil parent material	稳定值 Stable value/cm	pH_95%	pH_50%	pH_5%
板页岩 Plate shale	51.34	4.67	4.02	3.37
第四纪红土 Quaternary red earth	34.76	5.17	4.36	3.56
河流冲积物 River alluvium	53.40	5.09	4.32	3.55
红砂岩 Tertiary red sandstone	42.43	5.01	4.31	3.61
花岗岩 Granite	36.70	4.32	4.26	4.20

土壤初始有效磷和交换性镁含量改变了小麦生长对pH的响应

Soil Initial Available Phosphorus and Exchangeable Magnesium Shaping the Response of Wheat Growth to pH

RichHTML

PDF

可视化

摘要/Abstract

引用本文

使用本文

图/表 9

参考文献 21

相关文章 15

编辑推荐

Metrics

小麦生长 Wheat growth	阈值 Critical value	有机质 Organic matter	pH	碱解氮 Available nitrogen	有效磷 Available phosphorus	有效钾 Available potassium	交换性氢 Exchangeable hydrogen	交换性铝 Exchangeable aluminum	交换性镁 Exchangeable magnesium	交换性钙 Exchangeable calcium
地上部生物量 Shoot biomass	pH_95%	-0.02	-0.15	-0.12	-0.27	0.33	0.53	-0.12	-0.23	-0.22
	pH_50%	-0.25	-0.65	-0.22	-0.89^*	-0.16	0.79	0.35	-0.80	-0.67
	pH_5%	-0.20	-0.40	-0.07	-0.46	-0.46	0.12	0.42	-0.42	-0.33
	稳定值Stable value	-0.03	0.93^*	-0.02	0.98^**	-0.14	-0.80	-0.77	0.90^*	0.88^*
根系生物量 Root biomass	pH_95%	-0.51	0.95^*	-0.50	0.87	0.04	-0.44	-0.83	0.94^*	0.99^**
	pH_50%	-0.62	0.87^*	-0.57	0.66	-0.26	-0.30	-0.90^*	0.71	0.85
	pH_5%	0.05	-0.58	0.11	-0.78	-0.55	0.45	0.27	-0.84	-0.70
	稳定值Stable value	-0.02	0.94^*	-0.06	0.95^*	-0.02	-0.67	-0.85	0.88	0.86
株高 Height	pH_95%	-0.81	-0.17	-0.75	-0.37	0.12	0.60	0.11	-0.12	0.01
	pH_50%	-0.12	-0.79	-0.07	-0.95^*	-0.27	0.68	0.57	-0.90^*	-0.79
	pH_5%	0.80	-0.48	0.78	-0.40	-0.36	-0.09	0.35	-0.63	-0.69
	稳定值Stable value	-0.34	0.81	-0.27	0.73	-0.42	-0.62	-0.71	0.70	0.79

[1]	罗鑫, 吴跃开, 张念念, 许杰, 杨再华. 油茶根际土壤真菌群落组成及多样性分析[J]. 中国农业科技导报, 2023, 25(2): 199-210.
[2]	吴红艳, 于淼, 冯健, 刘晖. 解磷生物肥对温室土壤磷有效性及辣椒产量的影响[J]. 中国农业科技导报, 2023, 25(10): 189-197.
[3]	张磊, 罗泽华, 杨明川, 李世贵, 辛玉华, 蔡斌, 刘好宝, 曾代龙, 顾金刚, 段碧华. 雪茄烟叶原料发酵微生物多样性及酶活变化研究[J]. 中国农业科技导报, 2021, 23(10): 171-180.
[4]	杨锁宁1,2，张黎1，刘春2，袁素霞2，张军云3，张盖天2. 温度和土壤酸度对八仙花‘Bailmer’生长发育的影响[J]. 中国农业科技导报, 2020, 22(5): 24-34.
[5]	张明明1,2§,刘丽华2§,赵建宗3,张力科3,刘阳娜2,李宏博2,张风廷2,姚骥4,庞斌双2,赵昌平2. 小麦种子规模化DNA提取及检测体系的优化[J]. 中国农业科技导报, 2019, 21(7): 161-169.
[6]	吴婕1,2,宫江宁3. 大孔树脂纯化金银花总黄酮及其对α-葡萄糖苷酶抑制活性的研究[J]. 中国农业科技导报, 2019, 21(10): 89-97.
[7]	林李华,支胡钰. 蚕沙土壤调理剂对酸性土壤改良及豆角生长的影响[J]. 中国农业科技导报, 2018, 20(4): 108-114.
[8]	刘熙东1,陈铃诗1,徐汉虹2*. 基于专利分析印楝素产业发展特征及其对策研究[J]. 中国农业科技导报, 2018, 20(2): 19-26.
[9]	王春燕1,胡堂路1,姜峰2,谭伟明1,段留生1*. 环境因子对冠菌素水溶液稳定性的影响[J]. 中国农业科技导报, 2018, 20(2): 116-121.
[10]	刘勤1,张熠2,杨玉明3,胡良龙1,郑砚砚1,檀律科1,黄旭1,唐耘1,王叶萌1. 基于专利大数据的油菜产业发展研究[J]. 中国农业科技导报, 2018, 20(10): 1-8.
[11]	边晨凯,张宇,陈度宇,许雷*. 一株咔唑降解菌的鉴定及其降解特性研究[J]. 中国农业科技导报, 2017, 19(5): 51-59.
[12]	王海斌1,2,张清旭1,陈晓婷1,马小毛1,赵虎1,叶江华2,3,孔祥海1. 动物源有机肥对茶树根际土壤酸度及微生物的影响[J]. 中国农业科技导报, 2017, 19(5): 115-122.
[13]	吴敏,韦家少*,孙海东,何鹏,吴炳孙,高乐. 生物质炭对橡胶园土壤酸度及交换性能的影响[J]. 中国农业科技导报, 2017, 19(3): 98-107.
[14]	刘小芸1,2,姚冬生1,2,3*. 饲用酶蛋白的理性设计及其改良技术[J]. , 2013, 15(5): 46-52.
[15]	程菲菲1,2,赵军旗2,石鹏君2,李江1,姚斌2. 瓶霉Phialophora sp. P13木聚糖酶基因的克隆及酶学性质分析[J]. , 2012, 14(1): 85-90.