Scientia Agricultura Sinica ›› 2019, Vol. 52 ›› Issue (9): 1553-1563.doi: 10.3864/j.issn.0578-1752.2019.09.007

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

Effect of Straw Addition on the Formation of Aggregates and Accumulation of Organic Carbon in Dryland Soil

WANG BiSheng1,YU WeiShui1,WU XuePing1(),GAO LiLi1,2,LI Jing1,3,LI ShengPing1,SONG XiaoJun1,LIU CaiCai1,4,LI Qian1,5,LIANG GuoPeng1,CAI DianXiong1,ZHANG JiZong1()   

  1. 1 Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081
    2 Institute of Environment and Sustainable Development in Agriculture, Chinese Academy of Agricultural Sciences, Beijing 100081
    3 College of Water Resources and Environment, Hebei GEO University, Shijiazhuang 050031
    4 College of Geographical Sciences, Shanxi Normal University, Linfen 041004, Shanxi
    5 College of Resource Environment and Tourism, Capital Normal University, Beijing 100048
  • Received:2018-11-07 Accepted:2019-01-21 Online:2019-05-01 Published:2019-05-16
  • Contact: XuePing WU,JiZong ZHANG E-mail:wuxueping@caas.cn;zhangjizong@caas.cn

Abstract:

【Objective】To understand the regularity of aggregation and organic carbon changes after adding straw in long-term conventional tillage soil and to explore the main reason of improved soil organic carbon, the effects of straw incorporation on soil aggregates and the organic carbon content in aggregate were determined, so as to provide theoretical basis for carbon fixation in dryland agriculture.【Method】 An in-lab incubation experiment was conducted for 180 days in a constant temperature incubator at 25℃ with the soil collected from conventional tillage and no-tillage field plot. Four treatments were set up, namely conventional soil without straw (CT), no-tillage soil without straw (NT), conventional tillage soil with straw (CTS) and no-till soil with straw (NTS). Each treatment was sampled 15 replicates periodically for aggregate and organic carbon determinations. The straw was the aboveground parts of maize collected from conventional tillage, and the dosage was 5% dry soil weight.【Result】 (1) Aggregate in CT and NT were dominated by 250-53 μm fraction, accounting for 52%-66% of total aggregates, while in CTS and NTS, the aggregates were dominated by 2 000-250 μm fraction, accounting for 41%-50% of total aggregates. CTS and NTS improved 2 000-250 μm aggregate by 230%-302% and 92%-134% relative to CT and NT, respectively. (2) Straw incorporation significantly increased the mean weight diameter (MWD), geometric mean diameter (GMD) and macro-aggregate content (R0.25) of water-table aggregates. In the 180th day, CTS increased 133%, 130%, and 235%, respectively; compared with CT, NTS increased 53%, 75% and 87%, respectively, compared with NT. (3) In the 180th day, compared with CT, CTS increased the organic carbon content in aggregate of 250-53 μm and <53 μm by 70% and 54%, respectively, and compared with NT, NTS increased in the same aggregates by 30% and 25%, respectively. (4) The contribution of organic carbon in 2 000-250 μm aggregate to soil organic carbon was significantly increased by CTS and NTS, with improvement of 49%-61% and 50%-60%, respectively, which was more affected by aggregate composition. 【Conclusion】 The addition of straw could effectively increase the content of macroaggregates (>250 μm) in the dryland, enhance its stability and increase the contribution of macroaggregates to soil organic carbon, and had a greater effect on the conventional tillage soil.

Key words: straw addition, dryland soil, aggregate, organic carbon

Fig. 1

The proportion of soil water-stable aggregate composition in each phase Error bars represent standard errors. Different lowercase letters indicate significant differences between treatments (P<0.05)"

Table 1

Soil aggregate stability under different incubation periods"

培养时间 Incubation time (d) 处理Treatment MWD (mm) GMD (mm) R0.25 (%)
0 CT 0.26±0.00b 0.13±0.00b 14.34±0.46b
NT 0.43±0.01a 0.17±0.01a 16.28±0.42a
15 CT 0.24±0.00d 0.11±0.00c 13.12±0.16d
NT 0.32±0.00c 0.15±0.00b 21.77±0.65c
CTS 0.67±0.03a 0.28±0.01a 47.48±1.85a
NTS 0.60±0.00b 0.27±0.01a 44.12±0.16b
30 CT 0.24±0.00d 0.12±0.00d 11.85±0.25d
NT 0.33±0.00c 0.16±0.00c 20.36±0.19c
CTS 0.66±0.01b 0.30±0.01b 44.35±0.54b
NTS 0.72±0.01a 0.35±0.01a 50.62±0.67a
60 CT 0.24±0.00d 0.13±0.00d 12.30±0.31d
NT 0.33±0.01c 0.17±0.00c 20.62±1.10c
CTS 0.64±0.00a 0.34±0.00a 48.07±0.08a
NTS 0.60±0.01b 0.32±0.00b 45.92±0.62b
90 CT 0.23±0.00c 0.12±0.00d 12.04±0.10c
NT 0.35±0.01b 0.18±0.00c 22.74±0.89b
CTS 0.64±0.00a 0.35±0.00b 49.40±0.59a
NTS 0.66±0.01a 0.36±0.01a 50.93±0.63a
180 CT 0.26±0.00d 0.14±0.00d 13.43±0.44d
NT 0.39±0.01c 0.20±0.01c 25.84±0.87c
CTS 0.60±0.01b 0.32±0.00b 45.03±0.51b
NTS 0.66±0.00a 0.36±0.00a 50.61±0.42a

Fig. 2

Soil organic carbon content in aggregate Error bars represent standard errors. Different lowercase letters indicate significant differences between treatments (P<0.05)"

Fig. 3

Contributing rates of organic carbon in aggregate to soil organic carbon Error bars represent standard errors. Different uppercase letters indicate significant differences between aggregates and different lowercase letters indicate significant differences between treatments (P<0.05)"

Table 2

The increment of aggregate organic carbon contribution rate (W, %), aggregates distribution (P, %) and aggregate organic carbon content (OC, g C·kg-1 aggregate) in added straw treatment soil compared with unprocessed soil"

培养时间
Incubation time
处理
Treatment
>2000 μm 2000—250 μm 250—53 μm <53 μm
W P OC W P OC W P OC W P OC
15 d CTS 2.2 2.7 6.7 17.7 30.5 -26.1 -20.7 -24.2 1.9 -9.6 -8.9 -3.1
NTS -1.4 -0.7 2.0 15.1 19.6 10.0 -8.3 -14.0 9.5 -5.7 -4.8 -0.2
30 d CTS 3.4 3.1 7.4 26.2 26.9 -25.9 -11.4 -18.0 1.7 -8.7 -12.0 -1.8
NTS -0.2 0.9 -2.6 11.8 24.4 -4.1 -12.7 -15.2 8.4 -8.7 -10.2 -0.3
60 d CTS 1.1 0.9 4.3 27.0 32.8 -28.2 -6.5 -16.9 2.5 -11.0 -16.8 -2.3
NTS -2.1 -1.5 -0.7 17.4 22.1 -4.3 -2.2 -8.8 9.6 -8.1 -11.8 1.4
90 d CTS 0.3 0.3 1.5 28.9 34.7 -31.2 -12.5 -18.3 1.2 -11.8 -16.8 -3.1
NTS -2.1 -1.4 -5.0 21.2 27.0 -5.4 -7.0 -12.5 8.3 -9.3 -13.1 -0.4
180 d CTS 0.7 0.5 16.5 26.5 30.2 -26.8 -4.9 -13.5 9.6 -11.1 -17.2 1.1
NTS -1.8 -1.1 -1.0 20.0 26.4 -5.9 -6.5 -11.0 7.5 -9.8 -14.3 0.0
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