Scientia Agricultura Sinica ›› 2020, Vol. 53 ›› Issue (20): 4215-4225.doi: 10.3864/j.issn.0578-1752.2020.20.010

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

Effects of Lime and Straw Addition on SOC Sequestration in Tier Soil

CAO BinBin(),ZHU YiHui,JIANG YuHan,SHI JiangLan,TIAN XiaoHong()   

  1. College of Natural Resource and Environment, Northwest A&F University /Key Laboratory of Plant Nutrition and the Agro-environment in Northwest China, Ministry of Agriculture and Rural Affairs, Yangling 712100, Shaanxi
  • Received:2020-02-10 Accepted:2020-06-24 Online:2020-10-16 Published:2020-10-26
  • Contact: XiaoHong TIAN E-mail:caobb0606@163.com;txhong@hotmail.com

Abstract:

【Objective】Soil organic carbon (SOC) sequestration is crucial for improving soil fertility and agricultural production sustainability. The soil inorganic carbon (SIC) is closely related to SOC with regarding with inter-transformation, which has also great effect on carbon sequestration. Crop straw return has been recognized as one of the most important organic amendment improving soil organic carbon sequestration in farmland. Meanwhile, the addition of lime also contributes greatly to increasing SIC, thereby affecting the SOC sequestration. However, the mechanism of simultaneous incorporation of crop straw and lime affecting on the CO2 emission, SOC and SIC dynamics are not well understood, and how the SOC sequestration responds to the initial level of SOC is not clear, particularly after straw return. 【Method】 The incubation experiment and stable isotope technique (13C) were used in the study. The two tested soils were collected from a field with continuously cropping of winter wheat for 16 years, which was subjected to differential crop residue and nitrogen managements over long-term, including (1) S0N0 soil (no straw return+ nitrogen fertilizer application: 0); (2) S1N1 soil (high amount of straw return+ nitrogen fertilizer application: 240 kg·hm-2). And then the two soils were both incubated with or without addition of straw and lime for 120 days under 25℃. 【Result】 The study showed that the soil cumulative CO2 emission was observed 42.9% higher in S1N1 soils than that in S0N0 soils, when without straw and lime addition. In both soils, the straw addition alone increased the soil cumulative CO2 emission by averages of 81.6% and 70.4%, respectively, compared with straw absence. Meanwhile, the increase of the cumulative CO2 emission in S0N0 soils was higher than in S1N1 soils. This showed that straw addition had a greater impact on the native OC mineralization in soil with low initial SOC. Lime addition decreased soil cumulative CO2 emission in both soils whether straw addition or not. Straw addition increased the SOC by 2.95 g·kg-1 and 3.19 g·kg-1 in S0N0 soils and S1N1 soils, respectively, while reduced the SOC by 1.36 g·kg-1 in S1N1 soils and did not affect the SOC in S0N0 soils when combining with lime addition. Using13C stable isotope technology, the newly formed organic carbon (OC) in the two soils both significantly increased after straw addition, therein which increased 25.8% in S0N0 soils when compared with S1N1 soils. However, the conjoint addition of lime and straw did not modify the newly formed SOC when compared with the addition of straw alone, which showed that the lime addition had no effect on the decomposition process of straw in the soil. Over all, straw addition alone increased the SOC net sequestration by 3 066.3 mg?kg-1and 2 480.53 mg?kg-1 in S0N0 soils and S1N1 soils, respectively. The conjoint addition of lime and straw had no significant effect on the SOC net sequestration in S0N0 soils, but there was a decreasing trend on the SOC net sequestration in S1N1 soils. Lime addition reduced the cumulative CO2 emission by 469 mg?kg-1 and 529 mg?kg-1 in S0N0 soils and S1N1 soils, respectively, which approximately equaled to the increases in SIC (by 443 mg?kg-1 and 566 mg?kg-1, respectively).【Conclusion】 In conclusion, the soil with low initial SOC content had higher potential in SOC sequestration. Lime addition might be an effective method to affect soil carbon sequestration and reduce soil CO2 emission through chemical reactions.

Key words: soil carbon, soil respiration, straw return, lime, isotope technology

Table 1

Basic physical and chemical properties of the two soils before incubation"

土样
Soil
pH SOC
(g?kg-1)
TN
(g?kg-1)
DOC
(mg?kg-1)
MBC
(mg?kg-1)
CaCO3
(g?kg-1)
NO3--N
(mg?kg-1)
NH4+-N
(mg?kg-1)
δ13C
(‰)
S0N0 8.21a 7.98b 0.77b 7.49b 177.8b 68.6a 6.86b 0.45b -24.514
S1N1 7.99b 12.61a 1.05a 195.7a 447.0a 65.5b 28.59a 1.38a -25.132

Fig. 1

Soil CO2 emission rate (a), cumulative CO2 emission (b) under different treatments The error bars outside the curve represent LSD0.05"

Table 2

Four-way repeated measure ANOVA with incubation time as factor for cumulative CO2 release"

时间
Time
时间×土壤
Time×soil fertility
时间×秸秆
Time×
straw
时间×石灰
Time×
lime
时间×土壤×秸秆
Time×soil fertility×straw
时间×土壤×石灰
Time×soil fertility×lime
时间×秸秆×石灰
Time×straw
×lime
时间×土壤×秸秆×石灰
Time×soil fertility×straw×lime
P P P P P P P P
CO2累积释放量
Cumulative CO2 emission
<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001

Table 3

Effects of straw and lime amendment on cumulative CO2 emission, SOC and SIC"

处理
Treatment
CO2释放量
CO2 emission (mg?kg-1)
增加量
Increase amount (mg?kg-1)
SOC
(mg?kg-1)
增加量
Increase amount (mg?kg-1)
SIC
(mg?kg-1)
增加量
Increase amount (mg?kg-1)
S0N0 M0 600b - 7280b - 8380a -
M1 3564a 2964 10480a 3200 8390a 10
S1N1 M0 1193b - 12440b - 7823a -
M1 4027a 2833 14435a 1995 7783a -40
S0N0 L0 2316a - 8825a - 8160b -
L1 1847b -469 8940a 115 8610a 443
S1N1 L0 2912a - 13575a - 7520b -
L1 2383b -529 13300b -275 8086a 566

Fig. 2

Difference of SOC content under different treatments Error bars represent standard errors of the mean values. Different lowercase letters indicate significant difference between different treatments at P<0.05"

Table 4

Differences between soil straw-derived organic carbon formation and decomposition of native organic carbon under different treatments"

处理
Treatment
丰度值
δ13C
13C abundance
(‰)
土壤有机碳
(Ctotal)
Final SOC
(g?kg-1)
源自秸秆碳比例(fnew)
New OC proportion (%)
源自秸秆碳
New OC
(g?kg-1)
源自原土壤碳比例(fnative)
Native SOC proportion (%)
源自土壤有机碳
Native SOC
(g?kg-1)
S0N0 L0 M0 -23.54 7.35e 0 0 100 7.35b
M1 -21.61 10.30d 28.9 2.98a 71.1 7.32b
L1 M0 -23.52 7.22e 0 0 100 7.22b
M1 -21.49 10.66d 32.4 3.45a 67.6 7.21b
S1N1 L0 M0 -25.28 12.48c 0 0 100 12.48a
M1 -23.48 14.67a 15.1 2.21b 84.9 12.46a
L1 M0 -25.42 12.40c 0 0 100 12.40a
M1 -23.46 14.20b 15.2 2.15b 84.8 12.04a

Fig. 3

Differences between soil organic carbon net sequestrations under different treatments Initial soil organic carbon content: S0N0: 7.98 g?kg-1, S1N1: 12.61g?kg-1. Lowercase letters in the figure indicate significant differences of final SOC between different treatments at P<0.05; Uppercase letters indicate significant differences of soil organic carbon net sequestration between different treatments at P<0.05"

Fig. 4

Difference of SIC content under different treatments Error bars represent standard errors of the mean values. Uppercase letters indicate significant differences between the two fertility soil treatments at P<0.05. Asterisk above the bars indicates statistically significant differences between lime-unamended and corresponding lime-amended soils"

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