Scientia Agricultura Sinica ›› 2026, Vol. 59 ›› Issue (19): 4277-4288.doi: 10.3864/j.issn.0578-1752.2026.19.007

• SOIL & FERTILIZER·WATER-SAVING IRRIGATION·AGROECOLOGY & ENVIRONMENT • Previous Articles     Next Articles

Effects of Continuous Cultivation and Cropland Afforestation on Nitrogen and Phosphorus Nutrients in Typical Steppe

BAO YuFan1(), ZHU Na1, ZHANG JingMin1, ZHAO Man2, LIU JiaHui1, LUO YuHong1, LI Le1, XU Nuo1, YAN YuChun1()   

  1. 1 Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences/State Key Laboratory of Efficient Utilization of Arable Land in China, Beijing 100081
    2 Hulunbuir Agricultural Reclamation Xieertala Farm Co., Ltd., Hulunbuir 021012, Inner Mongolia
  • Received:2025-11-25 Accepted:2026-03-12 Online:2026-10-01 Published:2026-10-10
  • Contact: YAN YuChun

Abstract:

【Objective】This study aimed to investigate the effects of long-term cultivation and cropland afforestation on soil nitrogen and phosphorus nutrients in typical grasslands of Inner Mongolia, so as to provide the scientific basis for rational utilization and sustainable development of grassland.【Method】Soil samples were collected in 0 to 50 cm soil layers from natural grassland, cropland (continuously cultivated for 60 years) and shrubland (afforestation for 17-18 years) of typical grassland in XilinGol, Inner Mongolia in August 2020. The content of soil total nitrogen (TN), total phosphorus (TP), ammonium nitrogen (NH4+-N), nitrate nitrogen (NO3--N) and available phosphorus (AP) were compared and analyzed under different land-use types.【Result】Grassland cultivation and the conversion of cropland to shrubland significantly affected soil nitrogen and phosphorus nutrients: (1) Reclamation and long-term cultivation of natural grassland significantly reduced the content of total nitrogen, total phosphorus, and ammonium nitrogen in the 0-10 cm soil layer, while significantly increasing the available phosphorus content in the 0-30 cm soil layer. (2) Following shrubland establishment through cropland conversion, no significant changes were observed in soil total nitrogen or ammonium nitrogen content; however, nitrate nitrogen content throughout the 0-50 cm profile, total phosphorus in the 20-50 cm soil layer, and available phosphorus in the 0-30 cm soil layer all decreased significantly. (3) In response to land-use change, soil nitrate nitrogen and available phosphorus-representing readily available nutrient pools-exhibited more pronounced changes compared to total nitrogen and total phosphorus.【Conclusion】Grassland cultivation significantly decreased the content of soil total nitrogen and total phosphorus, however, the current management model of planting leguminous shrubs combined with understory herb harvesting struggled to achieve effective soil nutrient recovery in the short term and might even exacerbate phosphorus deficiency.

Key words: grassland cultivation, conversion of cropland to shrubland, soil nitrogen, soil phosphorus, typical steppe

Table 1

Basic characteristics of study sites"

样地1 Site1 样地2 Site2 样地3 Site3 样地4 Site4 样地5 Site5
草地
Grassland
优势种
Dominant species
糙隐子草、羊草、苔草、克氏针茅 Cleistogenes squarrosa, Leymus chinensis, Carex duriuscula, Stipa krylovii
管理方式
Management
放牧
Grazing
放牧
Grazing
刈割
Mowing
刈割
Mowing
刈割
Mowing
耕地
Cropland
开垦年限
Cultivation duration (a)
60 60 60 60 60
作物类型
Crop type
向日葵
Helianthus annuus
小麦
Triticum aestivum
小麦
Triticum aestivum
小麦
Triticum aestivum
苜蓿
Medicago sativa
管理方式
Management
1960-2013:小麦-燕麦轮作
2013-2020:小麦-燕麦-向日葵轮作
灌溉
施肥
Triticum aestivum-Avena sativa rotation from1960 to 2013, Triticum aestivum-Avena sativa and Helianthus annuus rotation after 2013
Irrigation
Fertilization
1960-2020:小麦-燕麦轮作
施肥
Triticum aestivum-Avena sativa rotation from1960 to 2020
Fertilization
1960-2020:小麦-燕麦轮作
施肥
Triticum aestivum-Avena sativa rotation from1960 to 2020
Fertilization
1960-2020:小麦-燕麦轮作
施肥
Triticum aestivum-Avena sativa rotation from1960 to 2020
Fertilization
1960-2017:小麦
2017-2020:苜蓿
灌溉
施肥
Triticum aestivum planting from 1960 to 2017, Medicago sativa planting after 2017
Irrigation
Fertilization
灌木林地
Shrubland
土地利用历史
Land use history
开垦43年后退耕造林17年
Afforestation for 17 years following a 43-year cultivation
开垦43年后退耕造林17年
Afforestation for 17 years following a 43-year cultivation
开垦43年后退耕造林17年
Afforestation for 17 years following a 43-year cultivation
开垦43年后退耕造林17年
Afforestation for 17 years following a 43-year cultivation
开垦42年后退耕造林18年
Afforestation for 18 years following a 42-year cultivation
林下草地优势种
Understory dominant
species
黄蒿Artemisia scoparia
披碱草Elymus dahuricus
糙隐子草Cleistogenes squarrosa
大籽蒿Artemisia sieversiana
黄蒿Artemisia scoparia
糙隐子草Cleistogenes squarrosa
黄蒿Artemisia scoparia
无芒雀麦Bromus inermis
羊草Leymus chinensis
黄蒿Artemisia scoparia
羊草Leymus chinensis
阿尔泰狗娃花Heteropappus altaicus
管理方式
Management
刈割
Mowing
刈割
Mowing
放牧
Grazing
刈割
Mowing
放牧
Grazing

Table 2

The impacts of land-use types, soil layers and sites on soil nitrogen and phosphorus"

变量
Variable
全氮
Total
nitrogen, TN
全磷
Total phosphorus, TP
铵态氮
Ammonium nitrogen
硝态氮
Nitrate
nitrogen
速效磷
Available phosphorus
铵态氮/全氮
Ammonium nitrogen/TN
硝态氮/全氮
Nitrate
nitrogen/TN
速效磷/全磷
Available phosphorus/TP
F Sig. F Sig. F Sig. F Sig. F Sig. F Sig. F Sig. F Sig.
用地类型
Land-use type
53.512 *** 48.436 *** 10.335 *** 71.255 *** 71.747 *** 11.716 *** 58.027 *** 53.167 ***
土层Soil layer 125.073 *** 24.866 *** 7.442 *** 16.498 *** 30.032 *** 31.246 *** 2.522 * 8.489 ***
样点Site 104.697 *** 28.8 *** 9.841 *** 0.537 NS 25.589 *** 47.637 *** 14.011 *** 17.217 ***
用地类型×土层
Land-use type×
Soil layer
6.012 *** 1.006 NS 1.694 0.07 2.433 *** 9.551 *** 5.014 *** 0.671 NS 8.007 ***
用地类型×样点
Land-use type×Site
2.048 * 4.1 *** 15.657 *** 2.479 *** 6.983 *** 18.487 *** 6.343 *** 7.098 ***
土层×样点
Soil layer×Site
3.923 *** 1.993 * 1.174 0.292 1.322 NS 2.156 ** 3.999 *** 1.248 NS 1.062 NS
用地类型×土层×样点
Land-use type×
Soil layer×Site
1.414 * 0.709 NS 0.989 0.501 1.618 * 1.072 NS 2.197 *** 1.966 ** 0.968 NS

Fig. 1

The impacts of land-use types, soil layers and sites on soil nitrogen and phosphorus"

Fig. 2

The soil TN, NH4+-N, and NO3--N content as well as TN/NH4+-N and TN/NO3--N rate among land-use types in various soil layers GL: Grassland, CL: Cropland, SN: Shrubland with narrow row spacing, SW: Shrubland with wide row spacing. Different lowercase letters represent significant differences among land-use types for a given soil layer (P<0.05). The same as below"

Fig. 3

The change ratios in soil TN, NH4+-N and NO3--N content among different land-use types in various soil layers RGC: The change ratios of the conversion from grassland to cropland, RCS-n: The change ratios of the conversion from cropland to shrubland with narrow row spacing, RCS-w: The change ratios of the conversion from cropland to shrubland with wide row spacing. The same as below * Represents significant differences of change ratios among TN, NH4+-N and NO3--N. (* P<0.05, ** P<0.01)"

Fig. 4

The soil total phosphorus (TP) and available phosphorus (AP) content and TP/AP among different land-use types in various soil layers"

Fig. 5

Changes of soil ammonium nitrogen, nitrate nitrogen and available phosphorus with soil layers in different land-use types"

Fig. 6

The change ratios in soil TP and AP content among different land-use types in various soil layers * Represents significant differences of change ratios between soil TP and AP content (*: P<0.05, **: P<0.01)"

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