basic soil productivity of spring maize in black soil under long-term fertilization based on dssat...

11
Journal of Integrative Agriculture 2014, 13(3): 577-587 March 2014 RESEARCH ARTICLE © 2014, CAAS. All rights reserved. Published by Elsevier Ltd. doi: 10.1016/S2095-3119(13)60715-7 Basic Soil Productivity of Spring Maize in Black Soil Under Long-Term Fertilization Based on DSSAT Model ZHA Yan 1 , WU Xue-ping 1 , HE Xin-hua 1, 2 , ZHANG Hui-min 1 , GONG Fu-fei 1 , CAI Dian-xiong 1 , ZHU Ping 3 and GAO Hong-jun 3 1 Key Laboratory of Crop Nutrition and Fertilization, Ministry of Agricultural/Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081, P.R.China 2 School of Plant Biology, University of Western Australia, Crawley, WA 6009, Australia 3 Jilin Academy of Agricultural Sciences, Changchun 130033, P.R.China Abstract Increasing basic farmland soil productivity has significance in reducing fertilizer application and maintaining high yield of crops. In this study, we defined that the basic soil productivity (BSP) is the production capacity of a farmland soil with its own physical and chemical properties for a specific crop season under local environment and field management. Based on 22-yr (1990-2011) long-term experimental data on black soil (Typic hapludoll) in Gongzhuling, Jilin Province, Northeast China, the decision support system for an agro-technology transfer (DSSAT)-CERES-Maize model was applied to simulate the yield by BSP of spring maize (Zea mays L.) to examine the effects of long-term fertilization on changes of BSP and explore the mechanisms of BSP increasing. Five treatments were examined: (1) no-fertilization control (control); (2) chemical nitrogen, phosphorus, and potassium (NPK); (3) NPK plus farmyard manure (NPKM); (4) 1.5 time of NPKM (1.5NPKM) and (5) NPK plus straw (NPKS). Results showed that after 22-yr fertilization, the yield by BSP of spring maize significantly increased 78.0, 101.2, and 69.4% under the NPKM, 1.5NPKM and NPKS, respectively, compared to the initial value (in 1992), but not significant under NPK (26.9% increase) and the control (8.9% decrease). The contribution percentage of BSP showed a significant rising trend (P<0.05) under 1.5NPKM. The average contribution percentage of BSP among fertilizations ranged from 74.4 to 84.7%, and ranked as 1.5NPKM>NPKM>NPK≈NPKS, indicating that organic manure combined with chemical fertilizers (1.5NPKM and NPKM) could more effectively increase BSP compared with the inorganic fertilizer application alone (NPK) in the black soil. This study showed that soil organic matter (SOM) was the key factor among various fertility factors that could affect BSP in the black soil, and total N, total P and/or available P also played important role in BSP increasing. Compared with the chemical fertilization, a balanced chemical plus manure or straw fertilization (NPKM or NPKS) not only increased the concentrations of soil nutrient, but also improved the soil physical properties, and structure and diversity of soil microbial population, resulting in an iincrease of BSP. We recommend that a balanced chemical plus manure or straw fertilization (NPKM or NPKS) should be the fertilization practices to enhance spring maize yield and improve BSP in the black soil of Northeast China. Key words: spring maize, long-term fertilization, basic soil productivity, black soil, DSSAT model INTRODUCTION With a cropping area of 7.4 million ha and a population over 109.3 millions, the black soil (Typic hapludoll) region of northeastern China plays a crucial role in food security to the regional and whole country. However, the long-term intensive maize Received 9 October, 2013 Accepted 18 December, 2013 ZHA Yan, Tel: +86-10-82108665, E-mail: [email protected]; Correspondence WU Xue-ping, Tel: +86-10-82108665, E-mail: [email protected]; ZHANG Hui-min, Tel: +86-10-82105039, E-mail: [email protected]

Upload: hong-jun

Post on 30-Dec-2016

212 views

Category:

Documents


0 download

TRANSCRIPT

Journal of Integrative Agriculture2014, 13(3): 577-587 March 2014RESEARCH ARTICLE

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.doi: 10.1016/S2095-3119(13)60715-7

Basic Soil Productivity of Spring Maize in Black Soil Under Long-Term Fertilization Based on DSSAT Model

ZHA Yan1, WU Xue-ping1 , HE Xin-hua1, 2, ZHANG Hui-min1, GONG Fu-fei1, CAI Dian-xiong1, ZHU Ping3 and GAO Hong-jun3

1Key Laboratory of Crop Nutrition and Fertilization, Ministry of Agricultural/Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081, P.R.China

2 School of Plant Biology, University of Western Australia, Crawley, WA 6009, Australia3Jilin Academy of Agricultural Sciences, Changchun 130033, P.R.China

Abstract

Increasing basic farmland soil productivity has significance in reducing fertilizer application and maintaining high yield of crops. In this study, we defined that the basic soil productivity (BSP) is the production capacity of a farmland soil with its own physical and chemical properties for a specific crop season under local environment and field management. Based on 22-yr (1990-2011) long-term experimental data on black soil (Typic hapludoll) in Gongzhuling, Jilin Province, Northeast China, the decision support system for an agro-technology transfer (DSSAT)-CERES-Maize model was applied to simulate the yield by BSP of spring maize (Zea mays L.) to examine the effects of long-term fertilization on changes of BSP and explore the mechanisms of BSP increasing. Five treatments were examined: (1) no-fertilization control (control); (2) chemical nitrogen, phosphorus, and potassium (NPK); (3) NPK plus farmyard manure (NPKM); (4) 1.5 time of NPKM (1.5NPKM) and (5) NPK plus straw (NPKS). Results showed that after 22-yr fertilization, the yield by BSP of spring maize significantly increased 78.0, 101.2, and 69.4% under the NPKM, 1.5NPKM and NPKS, respectively, compared to the initial value (in 1992), but not significant under NPK (26.9% increase) and the control (8.9% decrease). The contribution percentage of BSP showed a significant rising trend (P<0.05) under 1.5NPKM. The average contribution percentage of BSP among fertilizations ranged from 74.4 to 84.7%, and ranked as 1.5NPKM>NPKM>NPK≈NPKS, indicating that organic manure combined with chemical fertilizers (1.5NPKM and NPKM) could more effectively increase BSP compared with the inorganic fertilizer application alone (NPK) in the black soil. This study showed that soil organic matter (SOM) was the key factor among various fertility factors that could affect BSP in the black soil, and total N, total P and/or available P also played important role in BSP increasing. Compared with the chemical fertilization, a balanced chemical plus manure or straw fertilization (NPKM or NPKS) not only increased the concentrations of soil nutrient, but also improved the soil physical properties, and structure and diversity of soil microbial population, resulting in an iincrease of BSP. We recommend that a balanced chemical plus manure or straw fertilization (NPKM or NPKS) should be the fertilization practices to enhance spring maize yield and improve BSP in the black soil of Northeast China.

Key words: spring maize, long-term fertilization, basic soil productivity, black soil, DSSAT model

INTRODUCTION

With a cropping area of 7.4 million ha and a population

over 109.3 millions, the black soil (Typic hapludoll) region of nor theastern China plays a c ruc ia l role in food security to the regional and whole country. However, the long-term intensive maize

Received 9 October, 2013 Accepted 18 December, 2013ZHA Yan, Tel: +86-10-82108665, E-mail: [email protected]; Correspondence WU Xue-ping, Tel: +86-10-82108665, E-mail: [email protected]; ZHANG Hui-min, Tel: +86-10-82105039, E-mail: [email protected]

578 ZHA Yan et al.

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

cropping with all straw harvested for rural fuel and unsustainable land use practices over the last 20 yr, has resulted in great decreases of soil organic carbon (SOC), and rapid declines of soil fertility and crop productivity (Yu et al. 2006; Xu et al. 2010; Kou et al. 2012). To meet an ever-increasing grain demand, a further exploration of the productivity potential of farmland while improving its soil fertility is urgently required.

The improvement of soil productivity depends on the optimal field management such as rational tillage, irrigation and fertilizer application, and the increase of basic soil productivity (BSP) with its own physical and chemical properties under the same climate condition. In previous studies, BSP was generally characterized by crop yields from the long-term no-fertilization control or the contribution percentage of BSP (Yields in the no-fertilization control treatment/Yields in a corresponding fertilization×100%) (Huang et al. 2006; Zhang et al. 2009; Ma et al. 2012; Zeng et al. 2012). In fact, soil nutrients keep continuous depletion under long-term no-fertilization control, so the yield of no-fertilization could not really reflect actual changes of BSP under long-term different fertilizations. Unfortunately, at present, the conception of BSP has not been clearly defined.

In order to accurately characterize the BSP and explore the changes of BSP, we define BSP as the productive capacity of a farmland soil with its own physical and chemical properties. Under the same field management, there are mainly two contributions, i.e., external fertilizer application and BSP, to crop yield. Therefore, the contribution of BSP would mainly determine the crop yield under the same contribution of external fertilizer application. In other words, the crop yield could be increased with the increase of BSP even the contribution of external fertilizer application remain unchanged. Kunzová and Hejcman (2010) summarized that over 50 yr, the annual wheat yield was decreased under the no-fertilization control than under the different farmyard manure and mineral fertilizers in the Caslav crop rotation experiment in the Czech Republic. They claimed that such a yield decrease was due to a reduced natural fertility in the non-fertilized soil than in the respective fertilized soil (Geyic Phaeozem, Chernozem or sandy loamy

Cambisol) (Kunzová and Hejcman 2009). In contrast, under a high natural fertility, winter wheat production was stable and even increased without fertilizer input over 50 yr in Geyic Phaeozem soil (Kunzová and Hejcman 2010). In addition, crop yields in both the 150 yr long-term Rothamsted and 90 yr long-term Dikopshof fertilizations had also been maintained at >1 000 kg ha-1 without fertilizer input (Jenkinson 1991; Schellberg and Huging 1997). These results indicate that BSP is a reliable soil fertility index to maintain crop production.

The change of BSP is a comprehensive process of matter and energy conversion, such as atmosphere deposition, nitrogen fixation, mineral weathering and humification, etc. Yield by BSP is an integrated index to express BSP. However, in most long-term experiments, there are no measured yields by BSP under different fertilizations.

The decision support system for agro-technology transfer (DSSAT) crop growth model, which integrates the effects of soil, weather, management, genetics, and pests on daily growth, has been widely used to simulate growth, development, and yields of >26 crops growing on a uniform area of land, as well as variations in soil water, carbon, and nitrogen that take place under the cropping system over time (Soler et al. 2007; Thorp et al. 2008; Timsina et al. 2008; Yang et al. 2009; Dzotsi et al. 2010; Liu et al. 2011a; He et al. 2012; Deligios et al. 2013). The model has also predicted the long-term trend in potential yield of spring maize of Northeast China (Yang et al. 2010, 2011; Liu et al. 2012). According to the definition of BSP in this paper, the DAAST model could well simulate crop yields by BSP under local field management and no external fertilizer input for a specific crop season. Therefore, the DSSAT model may effectively resolve the problem of obtaining the yields by BSP under different fertilization treatments.

In this study, the DSSAT-CERES-Maize model (ver. 4.0) was employed to simulate the yield by BSP of spring maize and analyze the change characteristics of BSP after long-term fertilizations in the black soil region of northeast China. Our aims were to develop the concept of BSP and then to explore the factors and fertilization practices that could affect the increase of BSP and the productive potential of farmland.

Basic Soil Productivity of Spring Maize in Black Soil Under Long-Term Fertilization Based on DSSAT Model 579

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

RESULTS

Yield evaluation

The spring maize yields after different fertilizations (1990-2011) were simulated by the DSSAT model. The results showed that the normalized root mean square error (RMSE) and the index of agreement (d) of spring maize ranged from 9.70 to 13.46% and 0.849 to 0.929, respectively, over the 22 yr long-term fertilizations (Fig. 1).

Trends of yield by basic soil productivity of spring maize

Yields of BSP of spring maize were significantly lower under the control than under any fertilization treatments (Fig. 2). Simulated yield by BSP of spring maize under NPK, NPKM, 1.5NPKM, and NPKS showed a similar increasing trend while a decreasing trend under the control over fertilization years. Compared to the year of 1992, after 20-yr of fertilization, maize yields by BSP was increased by 53.4, 78.0, 101.2, and 69.4%, respectively, with

an respectively annual increase of 3.1, 4.6, 6.0, and 4.1%. In addition, significant higher average yields by BSP between fertilizations ranked as 1.5NPKM (8 178 kg ha-1)>NPKM (7 245 kg ha-1)≈NPK (7 011 kg ha-1)≈NPKS (6 976 kg ha-1)>the control (3 405 kg ha-1).

Over the 20-yr fertilization under NPK, NPKM, 1.5NPKM, and NPKS, four periods could be divided to show the change of maize yields with the BSP: a rapid increase period from 1992 to 1995, with an similar annual increase of 18.8, 19.0, 20.9, and 18.4%, respectively; a yield fluctuation period from 1996 to 2003 with a varied 5 606-8 580 kg ha-1 yield production; a relatively flat yield rising period from 2004 to 2008, with an annual increase from 6.9 to 10.7%; and a yield decrease period from 2009 to 2011, with an annual decrease from 1.4 to 3.1% (Fig. 2).

Compared with data between the first three fertilization years (1992 to 1994) and the last three fertilization years (2009 to 2011), the average crop yields by BSP were significantly increased by 62.3, 46.7 and 39.2% (P<0.05) under 1.5NPKM, NPKM, and NPKS, respectively, but not significant under both NPK with a 26.9% increase and the control with a 8.9% decrease (Table 1).

Fig. 1 Relationships between measured and simulated yields of spring maize over 22-yr long-term fertilizations (1990-2011). A, NPK treatment. B, NPKM treatment. C, 1.5NPKM treatment. D, NPKS treatment. E, control. F, five treatments (NPK, NPKM, 1.5NPKM, NPKS and control).

RMSE=13.27%RMSE=13.46%

d=0.862

y=0.680x+2 124R2=0.754n=22

6 000 8 000 10 000 12 000

RMSE=9.70%d=0.906

y=0.632x+3 187R2=0.772n=22

6 000

7 000

8 000

9 000

10 000

11 000

12 000

6 000 8 000 10 000 12 000

A B C

D E F

d=0.849

y=0.564x+3 314R2=0.699n=22

6 000 8 000 10 000 12 000

RMSE=11.41%d=0.901

y=0.536x+4 188R2=0.521n=22

6 000

7 000

8 000

9 000

10 000

11 000

12 000

6 000 8 000 10 000 12 000

Sim

ulat

ed y

ield

(kg

ha-1)

Sim

ulat

ed y

ield

(kg

ha-1)

6 000

7 000

8 000

9 000

10 000

11 000

12 000

6 000

7 000

8 000

9 000

10 000

11 000

12 000

RMSE=10.87%d=0.929

y=0.734x+1 180R2=0.886n=20

1 000

2 000

3 000

4 000

5 000

6 000

1 000 2 000 3 000 4 000 5 000

RMSE=13.23%d=0.872

y=0.785x+ 366R2=0.864n=108

2 000

4 000

6 000

8 000

10 000

12 000

2 000 4 000 6 000 8 000 10 000 12 000

Measured yield (kg ha-1)

580 ZHA Yan et al.

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

available potassium (Fig. 4).

DISCUSSION

Basic soil productivity characterization

BSP was a comprehensive index in evaluating soil basic fertility (Gong et al. 2013). Some researchers used the control yield (Zhu e t al . 1997b; Xie et al. 2002; Jiang 2011), or yields under no nitrogen application (Meng et al. 2010; Wang et al. 2011), or contribution percentage of BSP as an index to characterize BSP (Xu et al. 2006; Tang and Huang 2008). The contribution percentage of BSP was expressed as the ratio of crop yields under no-fertilization versus under fertilization (Zhu et al. 1997a; Huang et al. 2006; Zhang et al. 2009), or the ratio of crop yield under no-fertilization versus under suitable fertilization (Tang and Huang 2008) or versus the average yield among inorganic and organic combination treatments (Huang 2006). Studies have shown that the contribution percentage of BSP showed a fluctuating but constant decreasing trend over 27-yr to the early rice and late rice in yellow paddy soil in southern China (Wang e t a l . 2 0 1 0 ) . M e a n w h i l e , t h e c o n t r i b u t i o n percentage of BSP decreased from 79% in 1988 to 42% in 1996 (after 8 yr) in the black soil region of northeast China (Gao et al. 2009). The reason for such declining was that they used the crop yields under no-fertilization as numerator to calculate the

1 0002 0003 0004 0005 0006 0007 0008 0009 000

10 00011 000

1992 1994 1996 1998 2000 2002 2004 2006 2008 2010

Sim

ulat

ed y

ield

by

BSP

(kg

ha-1)

Year

NPK NPKM 1.5NPKM NPKS CK

Fig. 2 Simulated yields by basic soil productivity of spring maize under long-term fertilizations (1992-2011).

Table 1 Simulated yield by BSP of spring maize in different periods under different fertilizations1)

TreatmentsMean yield (kg ha-1 yr-1)

(1992-1994)Mean yield (kg ha-1 yr-1)

(2009-2011)Control 3 922±1 139 a, x 3 574±743 d, xNPK 5 702±1 065 a, x 7 239±502 c, xNPKM 5 640±1 029 a, x 8 273±276 b, y1.5NPKM 5 908±1 238 a, x 9 590±176 a, yNPKS 5 631±996 a, x 7 838±267 bc, y1) Data were expressed as means±SE. Letters a, b, c between treatments for the

same period within a column indicated a significant difference at P<0.05 level. Letters x, y between periods for the same treatment within a row indicated a significant difference at P<0.05 level.

Contr ibut ion percentage of bas ic so i l productivity

The contribution percentage of BSP showed a general increase trend but fluctuated with time over the 20-yr fertilizations under all fertilization treatments, except a significant increase under 1.5NPKM (P<0.05) (Fig. 3). The average contribution percentage of BSP between fertilizations ranged from 74.4 to 84.7%, and ranked as 1.5NPKM>NPKM>NPK≈NPKS.

Analysis of correlation between soil nutrient and basic soil productivity

The contribution percentage of BSP was significantly correlated with the soil organic matter (SOM), total nitrogen, total phosphorus or available phosphorus (R2=0.08-0.124, n=56-68). In contrast, there are no correlations between the contribution percentage of BSP and available nitrogen, total potassium, or

NPK NPKM 1.5NPKM NPKS

40

50

60

70

80

90

100

1992 1994 1996 1998 2000 2002 2004 2006 2008 2010

Con

tribu

tion

perc

enta

ge o

f BSP

(%)

Year

Fig. 3 Contribution percentage of basic soil productivity under long-term fertilizations (1992-2011).

Basic Soil Productivity of Spring Maize in Black Soil Under Long-Term Fertilization Based on DSSAT Model 581

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

contribution percentage of BSP. The control yield gradually decreased with the continuous depletion of soil nutrient (Wang et al. 2000; Sui et al. 2005; Liu et al. 2011b). In this study, the control yield also decreased 8.9% over 20 yr (Fig. 2). Therefore, using the control yield to calculate the contribution percentage of BSP under various fertilizations could not accurately reflect the changes of BSP. Our study indicated that the application of the calibrated DSSAT model could well simulate yield by BSP of spring maize and resolved the problems that were derived from the measured control yield to characterize BSP.

In this study, the contribution percentage of BSP was expressed as the ratio of crop yield by BSP under different fertilizations vs. measured yield in corresponding fertilization. The contribution percentage of BSP increased under NPK, NPKM, 1.5NPKM and NPKS treatments, and ranked as 1.5NPKM>NPKM>NPK≈NPKS (Fig. 3).

Effects of different fertilizations on basic soil productivity

The trends of BSP varied from each other among

different fertilizations compared with their 20-yr data. The result showed that after 20-yr fertilization, s i m u l a t e d y i e l d s b y B S P o f s p r i n g m a i z e significantly increased under NPKM, 1.5NPKM, and NPKS, while decreased 8.9% under the control (Fig. 2 and Table 1).

The simulated average yields by BSP of spring maize (1992 to 2011) under NKP, NPKM, 1.5NPKM and NPKS were significantly higher than that of the control and were 2.06, 2.13, 2.40 and 2.05 times that of the control, respectively (Fig. 2). At the end of experiment (2009 to 2011), the yield of BSP of spring maize under NPK, NPKM, 1.5NPKM and NPKS increased 64.1, 88.9, 118.1 and 80.3% compared with that of the control, respectively. The yield of BSP under NPKM, 1.5NPKM and NPKS were significantly higher than that of the NPK and increased 14.3, 32.5 and 8.3% compared with that of NPK, respectively (Table 1). These results indicated that the manure or straw combined with chemical fertilizer application could more effectively increase the yields by BSP than that of single chemical fertilizer as a whole. Our results corresponded with the study on BSP of Shajiang black soil over 22-yr long-term fertilization (Cao et al. 2008).

40

50

60

70

80

90

100

5 15 25 35

Con

tribu

tion

perc

enta

ge o

f BSP

(%)

Soil total K content (g kg-1)

G

0 100 200 300Soil available K content (g kg-1)

F

y=11.88x+68.43R2=0.10*

n=56

0.3 0.8 1.3 1.8 2.3Soil total P content (g kg-1)

E

y=0.075x+73.86R2=0.10*

n=56

40

50

60

70

80

90

100

0 50 100 150 200Con

tribu

tion

perc

enta

ge o

f BSP

(%)

Soil available P content (mg kg-1)

D

y=9.753x+63.89R2=0.08*

n=6840

50

60

70

80

90

100

0.8 1.3 1.8 2.3 2.8 Con

tribu

tion

perc

enta

ge o

f BSP

(%)

Soil total N content (g kg-1)

C

50 100 150 200 250Soil available N content (mg kg-1)

B

y=0.736x+57.94R2=0.124**

n=68

40

50

60

70

80

90

100

15 25 35 45 55Con

tribu

tion

perc

enta

ge o

f BSP

(%)

Soil organic matter content (g kg-1)

A

Fig. 4 Relationships between contribution percentage of basic soil productivity and soil nutrient contents. * and ** indicate significant differences at P<0.05 and P<0.01 levels, respectively.

582 ZHA Yan et al.

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

Effec ts o f so i l nu t r i en t on bas ic so i l productivity

The reasons of BSP differences mainly lie in soil nutrient caused by fertilization management. The relationship between soil nutrient and BSP proved that soil nutrient, especially SOM was the key factor that affects BSP in black soil (Fig. 4), which corroborated with observation from Shajiang black soil in north Anhui Province (Zhang et al. 2005). Soil with high SOM had a high yield of BSP (e.g., 1.5NPKM, NPKM), whereas soil with a relative low SOM had a low one (e.g., the control) (Fig. 2 and Fig. 5-A). SOM showed a significant linear increasing trend under NPKM and 1.5NPKM over 20-yr long-term fertilization. In 2008, the SOM increased 21.7, 65.0, 65.0 and 25.9% under NPK, NPKM, 1.5NPKM and NPKS treatments, respectively, compared with the control. It has been believed that SOM plays vital roles in soil structure, water holding capacity, nutrient transformations and cycling (Galantini and Rosell 2006; Bhattacharyya et al. 2011; Zhao and Zhou 2011), and SOM could thus improve BSP.

Total nitrogen, total phosphorus and available phosphorus also play important role in BSP increasing in black soil. Compared to the values at the beginning

of the experiment (in 1990), application of farmyard manure plus inorganic fertilizer significantly increased the concentration of total phosphorus and available phosphorus with 72-148% and 10.7-21.3 times, respectively, in 2005 (Fig. 5-C and D), and increased the concentration of total nitrogen with 10-21% in 2008 (Fig. 5-B). Thus, the increase of soil N and P caused by inorganic fertilizer combined with organic fertilizer (Gao et al. 2011; Alijani et al. 2012) were main reasons for BSP increasing.

The BSP change is a complicated result of the soil physical and chemical properties, microbiology, as well as management practices. Except the effects of soil nutrient on BSP, improvement of the soil physical properties (Zhao and Zhou 2011), and structure and diversity of soil microbial population (Kong et al. 2008; Wang et al. 2008; Wei et al. 2008; Sradnicka et al. 2013) caused by increasing the application of manure or straw combined with chemical fertilizer were other main reasons that lead to the increase of BSP.

CONCLUSION

In this study, applying the calibrated DSSAT model well simulated yields by BSP of spring maize and

15

20

25

30

35

40

45

50

1990 1992 1994 1996 1998 2000 2002 2004 2006 2008

SOM

(g k

g-1)

A

0

0.5

1

1.5

2

2.5

3

1990 1992 1994 1996 1998 2000 2002 2004 2006 2008

Tota

l nitr

ogen

(g k

g-1)

B

0.2

0.7

1.2

1.7

2.2

1990 1992 1994 1996 1998 2000 2002 2004

Tota

l pho

spho

rus (

g kg

-1)

Year

C

0

50

100

150

200

250

1990 1992 1994 1996 1998 2000 2002 2004

Avai

labl

e ph

osph

orus

(mg

kg-1)

Year

D

NPK NPKM 1.5NPKM NPKS

Fig. 5 Dynamic changing of SOM (A), total nitrogen (B), total phosphorus (C) and available phosphorus (D) under different fertilizations in black soil.

Basic Soil Productivity of Spring Maize in Black Soil Under Long-Term Fertilization Based on DSSAT Model 583

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

resolved the problems that using the control yield to characterize BSP. Simulated yields by BSP of spring maize under NPKM, 1.5NPKM, and NPKS showed a significant increasing trend, but not significant under both NPK with a 26.9% increase and the control with a 8.9% decrease over 20-yr fertilization. The average contribution percentage of BSP between fertilizations ranged 74.4 to 84.7%, and ranked as 1.5NPKM>NPKM>NPK≈NPKS.

This study showed that SOM was the key factor in various nutrient factors that affecting BSP in black soil, and total nitrogen, total phosphorus and available phosphorus also played important role in BSP increasing. Compared with the inorganic fertilizer, the balanced mineral application combined with manure or straw application (e.g., NPKM and NPKS) not only increased the concentrations of soil nutrients, but also

improved the soil physical properties, and structure and diversity of soil microbial population, which resulted in an increase of BSP.

MATERIALS AND METHODS

General situation of study region

The long-term experiment was started in the 1990’s in the experimental plot of Jilin Academy of Agricultural Sciences in Gongzhuling City, Jilin Province, China (124°48´34´´E and 43°30´23´´N, 220 m a.s.l). The site is in a flat area with an annual temperature of 4-5°C, an annual rainfall of 450-600 mm (70% in June-August), a frost-free period of 125-140 d, an effective accumulated temperature of 2 600- 3 000°C, and an annual amount of evaporation of 1 200- 1 600 mm. The soil was a black soil. The basic physio-chemical characteristics before treatments are listed in Table 2.

Table 2 Chemical and physical properties of soil before treatmentsSoil layer(cm)

Organic matter(g kg-1)

Total N(mg g-1)

Total P (mg g-1)

Total K (mg g-1)

Available N(mg kg-1)

Olsen-P (mg kg-1)

Available K (mg kg-1)

pHBulk density

(g cm-3)0-20 22.8 1.4 0.61 18.42 114 11.79 158.33 7.6 1.1921-40 15.2 1.3 0.59 18.58 98 6.77 150.83 7.5 1.2741-64 7.1 0.57 0.44 18.33 41 3.14 154.17 7.5 1.3365-89 6.8 0.5 0.43 18.42 39 1.83 157.50 7.6 1.3590-150 6.3 0.38 0.40 18.50 37 1.79 155.83 7.6 1.39

Design of field experiment

Five treatments or fertilizations were included in the experiment: (1) Control (no fertilizers); (2) NPK (nitrogen, phosphorus and potassium fertilizer); (3) NPKM (NPK plus organic manure); (4) l.5NPKM (1.5 times of NPKM); (5) NPKS (NPK plus 7 500 kg ha-1 straw). Spring maize with one crop per year was used as the experimental crop. The ratio of organic nitrogen to inorganic nitrogen was 7:3, with N:P2O5:K2O=l:0.5:0.5. A list of the fertilizer treatments used is given in Table 3.

Phosphorus (calcium superphosphate, 12.5% P2O5), potassium (potassium sulfate, 50% K2O) and one third of nitrogen fertilizer (urea, 45%N) were applied as the base fertilizer with sowing and the remaining two thirds of nitrogen fertilizer was topdressed at a depth of 10 cm below the topsoil before jointing. Organic manure (pig manure or cow manure) was used as the base manure and chopped (3-5 cm) straw was spread in furrows after topdressing in mid-July.

Model selection and simulation method

In this study, one of the DSSAT cropping system models, CERES-Maize (ver. 4.0) was selected for the yield simulation. The concrete steps of BSP simulation were

as follows: (1) the parameters of soil, weather, field management, and crop variety required for the model were inputted; (2) according to the actual measured yield of spring maize under NPK in the long-term experiment, the parameter of crop variety was calibrated using the “trial and error” method until the model simulation result was in accord with the actual measured value; (3) the yields under other fertilizer treatments (e.g., NPKM, 1.5NPMK and NPKS) were simulated by means of the calibrated parameter and then were tested for consistency with the actual measured values; (4) the yield by BSP for the year was simulated by setting no fertilization in the appropriate season only and was obtained using the same set of parameters, with a fixed fertilization in other years. For example, if the amount of a fertilizer in the n year is set to be zero only, with the fixed parameters including

Table 3 Rates of fertilizers application in different treatments each year (kg ha-1)

TreatmentInorganic fertilizer Manure Straw Total amount

of applied NN P2O5 K2O N NControl 0 0 0 0 0 0NPK 165 82.5 82.5 0 0 165NPKM 50 82.5 82.5 115 0 1651.5NPKM 75 123.8 123.8 173 0 248NPKS 112 82.5 82.5 0 53 165

584 ZHA Yan et al.

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

fertilization in the (n-1) year, the yield by BSP in the n year would be obtained when running yield simulation.

Model input date

The simulation process of the DSSAT model is mainly performed via the four modules of weather, soil, genetic characteristics of crop, and field management.

Meteorological data were from the database of the National Weather Service, including the daily weather data of Gongzhuling region, Jilin Province from 1990 to 2011. The daily weather data include daily solar radiation quantity (SRAD), daily maximum temperature (TMAX), daily minimum temperature (TMIN), and daily rainfall (RAIN). In the case of difficulty to obtain the daily solar radiation quantity (Q), based on the daily sunshine hours and relevant astronomical parameters, the Q value was estimated by means of the empirical formula (1):

Q=Q0(a+b )SS0 (1)

Where, Q0 is astronomical radiation, S is actual measured sunshine hours, S0 is available sunshine hours, a and b are functions of S and S0 (Rietveld 1978).

The soil profile input data in this study were directly obtained from the soil sample analysis in the 0-20 cm (the National Soil Fertility and Fertilizer Effects Long-term Monitoring Experiment Station 1998). The layered soil parameters include organic carbon, soil texture, bulk density, lower limit, drained upper limit, saturated soil water concentrations, cation exchange capacity, etc.

The field management module include initial soil water concentration, crop cultivar, plant density, sowing date, harvest date, fertiliza tion, etc.

According to the actual measured yields of spring maize under NPK from 1990 to 2011, the parameter of crop variety was calibrated using the “trial and error” method (Li et al. 2001) until the model simulation was in accord with the actual measured value. After several calibrations, the parameter of crop variety of spring maize was finally determined (Table 4). The yields under NPKM, 1.5NPKM, NPKS, and the control were simulated by means of the calibrated parameter and then were tested for consistency with the actual measured values.

Calibration method

In this study, the normalized root mean square error (RMSE) and index of agreement (d) were used to measure the relative degree of difference between the simulated value and actual measured value and to test the goodness of fit between them, respectively. The calculations are shown in the equations (2) and (3):

( )

n

RSRMSE=

n

i ii 1001

2∑=

-

(2)

(3)( )

( )||||

-

-∑=

ii

n

iii

RS

RSd=1-

2´ ´

1

∑=

n

i 1

2

Where, Ri is the actual measured value, Si is the simulated

value, R is the average actual measured value, Si´=Si -R, Ri´=Ri -R, n is the number of simulated value samples.

It is generally considered that, RMSE<10% is excellent; 10%<RMSE<20% is good; 20%<RMSE<30% is moderate; RMSE>30% is bad; and that as d value is closer to one, the consistency between the simulated value and actual measured value is better.

Soil sampling and analyses

Soil samples were collected from the topsoil (0-20 cm) every year for all plots after harvest. Soil organic carbon concentration was measured by vitriol acid-potassium dichromate oxidation (Walkley and Black 1934). Total nitrogen and available nitrogen were determined by the method introduced by Lu (1999). Total phosphorus was measured by Murphy and Riley (1962), and available phosphorus (Olsen-P) by the Olsen-P method (Olsen et al. 1954). Total potassium was determined by Kundsen et al. (1982), and available potassium by Lu (1999). Soil bulk density was measured with iron ring (Lu 1999).

Data analysis

The contribution percentage of BSP was calculated using the following equation:

Contribution percentage of BSP (%)=Yield by BSP /Measured yield in corresponding fertilization×100The Microsoft Excel 2007 software was applied for data

processing and diagramming while the SAS 9.1 software was used for statistical analysis. Differences between yields by BSP between treatments or time periods were analyzed using the method of least significant difference (LSD) at P<0.05 or 0.01.

Acknowledgements We acknowledge all colleagues for their great efforts on the long-term experiments in black soil in Gongzhuling. The study was supported by the National 973 Program of China (2011CB100501), the National 863 Program of China

Table 4 Genetic parameters of spring maizeParameters P1 P2 P5 G2 G3 PHINTValues 260-280 0.70-0.75 850-950 650-850 8.0-12.0 38.9-42.9

P1, degree days (base 8°C) from the emergence to end of juvenile phase; P2, photoperiod sensitivity coefficient (0-1.0); P5, degree days (base 8°C) from silking to physiological maturity; G2, potential kernel number; G3, potential kernel growth rate, mg/(kernel d); PHINT, degree days required for a leaf tip to emerge (phyllochron interval) (°C d).

Basic Soil Productivity of Spring Maize in Black Soil Under Long-Term Fertilization Based on DSSAT Model 585

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

(2013AA102901), the Special Fund for Agro-Scientific Research in the Public Interest, China (201203077), and the Science and Technology Project for Grain Production, China (2011BAD16B15).

References Alijani K, Bahrani M J, Kazemeini S A. 2012. Short-term

responses of soil and wheat yield to tillage, corn residue management and nitrogen fertilization. Soil and Tillage Research, 124, 78-82.

Bhattacharyya T, Pal D K, Deshmukh A S, Deshmukh R R, Ray S K, Chandran P, Mandal C, Telpande B, Nimje A M, Tiwary P. 2011. Evaluation of Rothc model using four long term fertilizer experiments in black soils, India. Agriculture, Ecosystems & Environment, 144, 222-234.

Cao C F, Kong L C, Zhang C L, Zhao B, Zhao Z, Zhang Y L, Du S Z. 2008. Effect of fertilization on soil fertility, wheat yield and quality in Shajiang black soil. Chinese Journal of Eco-Agriculture, 16, 1073-1077. (in Chinese)

Deligios P A, Farci R, Sulas L, Hoogenboom G, Ledda L. 2013. Predicting growth and yield of winter rapeseed in a Mediterranean environment: Model adaptation at a field scale. Field Crops Research, 144, 100-112.

Dzotsi K A, Jones J W, Adiku S G K, Naab J B, Singh U, Porter C H, Gijsman A J. 2010. Modeling soil and plant phosphorus within DSSAT. Ecological Modelling, 221, 2839-2849.

Galantini J, Rosell R. 2006. Long-term fertilization effects on soil organic matter quality and dynamics under different production systems in semiarid Pampean soils. Soil and Tillage Research, 87, 72-79.

Gao H J, Peng C, Zhang X Z, Li Q, Zhu P, Fu J S. 2011. Effect of long-term straw returning field on the carbon and nitrogen in black soil and maize yield. Journal of Maize Sciences, 19, 105-107. (in Chinese)

Gao J, Ma C B, Xu M G, Xu Z Q, Zhang S X, Sun N. 2009. Change characteristic of fertilization and maize yield on black soil in the Northeast China. Soil and Fertilizer Sciences in China, 6, 28-31. (in Chinese)

Gong F F, Zha Y, Wu X P, Huang S M, Xu M G, Zhang H M, Liu H L, Jiang Z W, Wang X B, Cai D X. 2013. Analysis on basic soil productivity change of winter wheat in fluvo-aquic soil under long-term fertilization. Transactions of the Chinese Society of Agricultural Engineering, 29, 120-129. (in Chinese)

He J Q, Dukes M D, Hochmuth G J, Jones J W, Graham W D. 2012. Identifying irrigation and nitrogen best management practices for sweet corn production on sandy soils using CERES-Maize model. Agricultural Water Management, 109, 61-70.

Huang Q R, Hu F, Li H X, Lai T, Yuan Y H. 2006. Crop yield response to fertilization and its relations with climate and soil fertility in red paddy soil. Acta Pedologica Sinica, 43, 926-933. (in Chinese)

Huang S M. 2006. Studies on fertility evolution and

sustainable utilization of fluvo-aquic soil under different long-term fertilization patterns. PhD thesis, Henan Agriculture University, China. (in Chinese)

Jenkinson D S. 1991. The Rothamsted long- term experiments: are they still of use? Agronomy Journal, 83, 2-10.

Jiang J F. 2011. Impact on different fertilizer systems on contribution rate of dark loessial soil in Pingliang. Gansu Agricultural Science and Technology, 8, 28-30. (in Chinese)

Kong W D , Zhu Y G , Fu B J, Han X Z, Zhang L, He J Z. 2008. Effect of long-term application of chemical fertilizers on microbial biomass and functional diversity of a black soil. Pedosphere, 18, 801-808.

Kou T J, Zhu P, Huang S, Peng X X, Song Z W, Deng A X, Gao H J, Peng C, Zhang W J. 2012. Effects of long-term cropping regimes on soil carbon sequestration and aggregate composition in rainfed farmland of Northeast China. Soil and Tillage Research, 118, 132-138.

Kundsen D, Peterson G A, Pratt P F, Page A L. 1982. Lithium, sodium, and potassium. In: Methods of Soil Analysis , Part 2 . 2nd ed, Wisc: ASA and SSSA, Madison. pp. 225-246.

Kunzová E, Hejcman M. 2009. Yield development of winter wheat over 50 years of FYM, N, P and K fertilizer application on black earth soil in the Czech Republic. Field Crops Research, 111, 226-234.

Kunzová E, Hejcman M. 2010. Yield development of winter wheat over 50 years of nitrogen, phosphorus and potassium application on Greyic Phaeozem in the Czech Republic. European Journal of Agronomy, 33, 166-174.

Li J, Shao M A, Fan T L, Wang L X. 2001. Databases creation of crop growth model DSSAT3 on the loess plateau region of China. Agricultural Reseach in the Arid Areas, 19, 120-125. (in Chinese)

Liu H L, Yang J Y, He P, Bai Y L, Jin J Y, Drury C F, Zhu Y P, Yang X M, Li W J, Xie J G, et al. 2012. Optimizing parameters of CSM-CERES-Maize model to improve simulation performance of maize growth and nitrogen uptake in northeast China. Journal of Integrative Agriculture, 11, 1898-1913.

Liu H L, Yang J Y, Tan C S, Drury C F, Reynolds W D, Zhang T Q, Bai Y L, Jin J, He P, Hoogenboom G. 2011a. Simulating water content, crop yield and nitrate-N loss under free and controlled tile drainage with subsurface irrigation using the DSSAT model. Agricultural Water Management, 98, 1105-1111.

Liu Y, Peng C, Zhang H M, Zhang W J, Dai J J, Xu M G. 2011b. Dynamic change of organic matter in the black soil under long-term fertilization. Soil and Fertilizer Sciences in China, 5, 7-11. (in Chinese)

Lu R K. 1999. Analytical Methods of Soil Aagricultural Chemistry. China Agricultural Science and Technology Press, Beijing, China. pp. 147-152, 191, 269-270.

Ma C B, Lu C A, Ren Y, Zhan X Y, Li G H, Zhang S X.

586 ZHA Yan et al.

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

2012. Effect of soil fertility and long-term fertilizer application on the yields of wheat and maize in fluvo-aquic soil. Plant Nutrition and Fertilizer Science, 18, 796-802. (in Chinese)

Meng A H, Zhou J S, Ding J, Mei L F, Zhong J. 2010. Experiment summary of corn yield without nitrogen fertilizer application. Shanghai Agricultural Science and Technology, 3, 80. (in Chinese)

Murphy J, Riley J P. 1962. A modified of single solution method for the determination of phosphate in nature water. Analytica Chimica Acta, 27, 31-36.

Olsen S R, Cole C V,Watanabe F S, Dean A. 1954. Estimation of Available Phosphorus in Soils by Extraction with Sodium Bicarbonate, (USDA Circ. 939). Government Printing Office, Washington, US. p. 939.

Rietveld M R. 1978. A new method for estimating the regression coefficients in the formula relating solar radiation to sunshine. Agricultural Meteorology, 19, 243.

Schellberg J, Huging H. 1997. Yield development of cereals, row crops and clover in the Dikopshof long-term fertilizer trial from 1906 to 1996. Archives of Agronomy and Soil Science, 42, 303-318.

Soler C M T, Sentelhas P C, Hoogenboom G. 2007. Application of the CSM-CERES-Maize model for planting date evaluation and yield forecasting for maize grown off-season in a subtropical environment. European Journal of Agronomy, 27, 165-177.

Sradnicka A, Murugana R, Oltmannsb M, Rauppc J, Joergensena R G. 2013. Changes in functional diversity of the soil microbial community in a heterogeneous sandy soil after long-term fertilization with cattle manure and mineral fertilizer. Applied Soil Ecology, 63, 23-28.

Sui Y Y, Zhang X Y, Jiao X G, Wang Q C, Zhao J. 2005. Effect of long-term different fertilizer applications on organic matter and nitrogen of black farmland. Journal of Soil Water Conservation, 19, 190-192. (in Chinese)

Tang Y H, Huang Y. 2008. Statistical analysis of the percentage of soil fertility contribution to grain crop yield and driving factors in mainland China. Journal of Agro-Environment Science, 27, 1283-1289. (in Chinese)

Thorpa K R, DeJongeb K C, Kaleitac A L, Batchelord W D, Paz J O. 2008. Methodology for the use of DSSAT models for precision agriculture decision support. Computers and Electronics in Agriculture, 64, 276-285.

Timsina J, Godwin D, Humphreys E, Yadvinder S, Singh B, Kukal S S, Smith D. 2008. Evaluation of options for increasing yield and water productivity of wheat in Punjab, India using the DSSAT-CSM-CERES-Wheat model. Agricultural Water Management, 95, 1099-1110.

Walkley A, Black I A. 1934. An examination of the degtjareff method for determining soil organic matter and a proposed modification of the chromic acid titration method. Soil Science, 37, 29-38.

Wang F, Lin C, Li Q H, He C M, Li Y, Lin X J. 2010. Effects of long-term fertilization on rice yield and

contribution rate of basic soil productivity on the yellow paddy of southern China. Fujian Journal of Agricultural Sciences, 25, 631-635. (in Chinese)

Wang G H, Liu J J, Qi X N, Jin J, Wang Y, Liu X B. 2008. Effects of fertilization on bacterial community structure and function in a black soil of Dehui region estimated by Biolog and PCR-DGGE methods. Acta Ecologica Sinica, 28, 220-226. (in Chinese)

Wang W, Chen W C, Wang K R, Xie X L, Yin C M, Chen A L. 2011. Effects of long-term fertilization on the distribution of carbon, nitrogen and phosphorus in water-stable aggregates in paddy soil. Journal of Integrative Agriculture, 10, 1932-1940.

Wang X D, Zhang Y P, Lv J L, Fan X L. 2000. Effect of long term different fertilization on properties of soil organic matter and humic acids. Scientia Agricultura Sinica, 33, 75-81. (in Chinese)

Wei D, Yang Q, Zhang J Z, Wang S, Chen X L, Zhang X L, Li W Q. 2008. Bacterial community structure and diversity in a black soil as affected by long-term fertilization. Pedosphere, 18, 582-592.

Xie J X, Zhang B S, Tan H F, Zhou P H. 2002. The soil fertility evolution trend and the reasons in Danyang. Soils, 3, 149-155. (in Chinese)

Xu M G, Liang G Q, Zhang F D. 2006. The Evolution of Soil Fertility in China. China’s Agricultural Science and Technology Press, Beijing, China. pp. 301-313. (in Chinese)

Xu X Z, Xu Y, Chen S C, Xu S G, Zhang H W. 2010. Soil loss and conservation in the black soil region of Northeast China: A retrospective study. Environmental Science and Policy, 13, 793-800.

Yang J M, Dou S, Yang J Y, Hoogenboom G, Jiang X, Zhang Z Q, Jiang H W, Jia L H. 2011. Crop-soil nitrogen cycling and soil organic carbon balance in black soil zone of Jilin Province based on DSSAT model. Chinese Journal of Applied Ecology, 22, 2075-2083. (in Chinese)

Yang J M, Liu J H, Dou S, Yang J Y, Hoogenboom G. 2010. Evaluation and optimization of best management practices of maize for black soil in Jilin China using the DSSAT Model, I. Cultivar calibration and sensitivity analysis of maize yield parameters. Acta Pedologica Sinica, 48, 366-374. (in Chinese)

Yang Q, Xu Y L, Lin E D, 2009. Application of DSSAT crop model on prediction of potential yield of spring wheat in Ningxia. Agricultural Research in the Arid Areas, 27, 41-48. (in Chinese)

Yu G, Fang H, Gao L, Zhang W. 2006. Soil organic carbon budget and fertility variation of black soils in Northeast China. Ecological Research, 21, 855-867.

Zeng X M, Han B J, Xu F S, Huang J L, Cai H M, Shi L. 2012. Effect of optimized fertilization on grain yield of rice and nitrogen use efficiency in paddy fields with different basic soil fertilities. Scientia Agricultura Sinica, 45, 2886-2894. (in Chinese)

Basic Soil Productivity of Spring Maize in Black Soil Under Long-Term Fertilization Based on DSSAT Model 587

© 2014, CAAS. All rights reserved. Published by Elsevier Ltd.

Zhang C L, Chen L T, Cao C F, Kong L C, Ji Y M. 2005. Study on the contribution of Shajiang black soil fertilizer and the appropriate technical measures of applying fertilizer. Chinese Agricultural Science Bulletin, 21, 244-246. (in Chinese)

Zhang X M, Guo X S, Wu J, Wang Y Q, Li X H, Chen J D. 2009. Research on basic soil fertility and reasonable fertilization technology in paddy fields in the Jianghuai Region. Chinese Agricultural Science Bulletin, 25, 131-135. (in Chinese)

Zhao J W, Zhou L R. 2011. Combined application of organic

and inorganic fertilizers on black soil fertility and maize yield. Journal of Northeast Agricultural University, 18, 24-29.

Zhu H X, Shen A L, Zhang X. 1997a. Nutrients supplying characteristics and evolution regularities of yellow fluvo-aquic soil. Chinese Journal of Soil Science, 34, 138-145. (in Chinese)

Zhu H X, Zhang X, Sun C H, Wang Y L. 1997b. Effect of long-term fertilization on wheat, corn yield and the influence on soil nutrient. Chinese Journal of Soil Science, 28, 160-163. (in Chinese)

(Managing editor SUN Lu-juan)