Introduction
As important grain crops, wheat and rice have been widely planted around
the world and have played an important role in human lives and industrial
production. For example, wheat is a cereal plant extensively grown worldwide
and used as one of the staple foods of human being. Wheat flour is generally
used for producing bread, taro, biscuits, noodles, etc. It can be also fermented into beer, alcohol,
liquor (e.g., vodka) or biomass fuel (Green et al. 2015; Das et
al. 2016). As a staple food planted in
Northeast and South China, the domestic cultivation area of conventional rice
is 245 million mu, and 200 million mu of hybrid rice. In addition to being edible, it can be used for
producing wine, sugar and industrial raw materials. Rice husks and rice straw
can be also utilized as livestock feed (Matsumura et al.
2005; Kafle and Chen 2016).
Applying chemical fertilizers is an important measurement for ensuring
high grain yields. According to Food
and Agriculture Organization (FAO) of the United Nations, it showed that
fertilizer application accounts for 60−67% of crop yield (Bouwman et
al. 2005). Soil fertility monitoring
in China showed that fertilizer application contributes 57.8% to grain
production (Wang et
al. 2011; Teng et al. 2014). In the 1980s, a large area of cultivated land in China
was deficient in main soil nutrients or deficient in some soils. A total of 78%
of China's total cultivated land areas are low- and medium-yielding fields (Wu et al. 2003; Zhang et al. 2016). Excessive fertilisation can result in soil nutrient
loss (Doan et al. 2015). For example, land surface runoff is one of the main pathways for the
nitrogen (N) and phosphorus (P) nutrient loss in farmland and third largest
pollution source in rivers and lakes in the United States (Beusen et al.
2016). At
present, considerable attentions have been paid to the studies on the losses of
land surface runoff of agricultural compounds (N, P, K).
The
absolute amount of nutrients absorbed by rice and wheat in a growth cycle is
positively correlated with the amount of fertilizer applied within a certain
range. At low fertilisation level, the amount of N and K
absorbed by the crop increases with the amount of applied fertilizer (Niu et al.
2013). Balanced application of N,
P, K fertilizers is crucial for the crop growth, but the amount of N in rice
and wheat plants was higher than other fertilizers (Aggarwal et al.
2006). The reason may be due to
the fact that the coordination of nutrient between two or more
nutrients is various in different cropping systems. For example, the P, N, and
N, K showed the positive interactions, which
promotes the absorption and utilization of nutrients by rice and wheat. K can
promote the absorption, transportation and accumulation of N, thereby
increasing the utilization of N (Landeweert et al. 2001).
Consequently, it is extremely important to investigate the relationship among
fertilisation application, soil
nutrient and crop yield in a rice-wheat rotation system (Sun et al.
2018). In this study, rational fertilisation was achieved for improving crop
yield and economic benefits in a typical rice-wheat cropping system.
Additionally, the differences in soil nutrients, nutrient runoff losses, crop
nutrient and yield were also observed.
Materials
and Methods
Experimental
material
The rice-wheat rotation system was adopted in the
experimental area. The specific fertilizers were carbamide, potassium
chloride, calcium superphosphate and other binary or three-nutrient compound
fertilizers. The wheat variety Yangmai 13 and the rice variety Wandao 158 were
grown.
Experimental location and climate
The study
area is located in Jianhua Village, Zhonghan Town, Juchao District, Chaohu City
(117°47′35", 31°38′45") at a distance of 2 km from Chaohu
Lake and 17 m above sea level. It has a subtropical humid monsoon climate. The
annual precipitation is 996.0 mm and the annual average temperature is 16°C.
The hottest month is July with monthly average temperature of 28.7°C and the
coldest month is January with monthly average temperature of 2.7°C. The annual
frost-free period is 247 d and the sunshine hours are 2106 h. The soil type for
the field experiment site is the subspecies of gleyed paddy soil. The soil
nutrients for the 0‒20 cm soil layer in the study area are: pH of 6.99,
organic matter (OA) of 34.07 g/kg, total nitrogen (TN) of 1.58 g/kg, total
phosphorus (TP) of 0.78 g/kg, available potassium (AK) of 136.31 mg/kg,
available phosphorus (AP) of 25.97 mg/kg and
Fig. 1: Schematic
plot of the experimental design
alkali-hydrolyzale nitrogen (Alkeline-N) of 168.54
mg/kg.
Experimental design
Six treatments included were non-N-fertilised
control (CK), conventional N
management (CON) based on local custom, optimised N
management (OPT), 30% reduced N (OPT-N) compared to OPT, 50% reduced P (OPT-P) on the basis of
OPT and straw with chemical fertilizer (OPT-NP+S) @200
kg of wheat straw per acre on the basis of OPT-N and OPT-P. Each treatment had
three repetitions on the experimental plot with an area of 30 m2
(Fig. 1).
Data collection
The
experimental soil nutrients, nutrient runoff losses and crop nutrient and yield
were collected during the years of 2015‒2017. Data were compiled by the
Microsoft Excel (Office 2016) software. Data analysis was performed by applying
the analysis of variance (ANOVA, P < 0.05) in SPSS 23.0 software
(SPSS® Inc., Chicago, IL, USA). Least significant difference (LSD) test was
used for multiple comparisons.
ANOVA
Factor A is
set with different levels of k denoted as A1, A2,
…, Ak. The ni (i=1,
2, …, k) test is repeated at each level and the indicators can be
obtained. The overall sample size is required to investigate whether the change
in single factor A has a significant effect on test indicator y of N=sum(ni)
(Chakraborty and Chowdhury 2016). The ui is set to represent the true
average of the test indicator y at the level of Ai.
The results of each experiment should exhibit random fluctuations around the
true average. Then, under the Ai, the result of each test Aij
should show random fluctuation around the true average. This random fluctuation
is recorded as ɛij. The ANOVA model is yi j=
ui + ɛij (i=1, 2, …, k, j=1,
2, …, ni) where ɛij ~ N(0, σ2)
are independent and ui and σ2 are
unknown. The significance of influence of factors is shown by whether k
totals have the same average. The test hypothesis is H0: ui
= ui = … = uk.
The sum of the squared
deviations of all the data is shown as follows:
(1)
The total sum of
squares is the sum of squares between groups and within groups:
(2)
The sum of squares between groups
is attributed to a change in A and reflects the difference between the overall
average, and the sum of squares within the group is caused by random factors.
Theoretically, the degree of freedom for SST, SSB
and SSW are respectively n-1, k-1 and n-k.
Under the assumption of normal distribution, if the groups of means are equal
as the originally assumed, then the statistical parameter F obeys an
F-distribution, which has a degree of freedom k-1 and n-k.
(3)
SST for a given sample is determined. If the original assumption keeps true, SSB
is extremely small and SSW is extremely large by
decomposition. Thus, F is extremely small. Conversely, if F is
extremely large, SSB is extremely large in the case where SST
is determined, and SSW is small by decomposition. The
original hypothesis is valid. Therefore, the F can be used in
determining whether the original hypothesis is true. The P-value (sig. =
p) can be calculated on the basis of F-distribution. When P <
alpha (the default value is 0.05), the original hypothesis is rejected. This
result shows that the factor A has a significant effect on the test indicators.
The P < 0.01 is indicative of a highly significant effect.
Statistical
analysis
The LSD test was introduced and T-test was performed for pairwise
comparison between groups due to its high sensitivity. Slight differences in
the mean between levels may be also tested (Sun et al. 2014).
If the data for each group
are n, the standard error (SE) of the LSD is:
(4)
Or,
(2)
Where MSE
is the mean square error and n is the number of data for each level of A
factor. If A has the k levels and the total data are N, then
(3)
Results
Soil nutrients under rice-wheat rotation system
after harvest
The mean of soil nitrate N content did not
significantly differ among treatments (Table 1). The ammonium N content
followed the order of OPT-N > CK > OPT-P > OPT-NP+S > CON > OPT. The OA had
an increasing trend for different fertilization treatments. The average value
of AP was significantly different among treatments of CON, OPT, OPT-N, CK,
OPT-P and OPT-NP+S. The maximum average content of AP was obtained under the
OPT-N. The mean content of AK followed the order of OPT-N > OPT-NP+S > OPT
> OPT-P > CK > CON and it reached 180.0 mg/kg for the OPT-N. The pH
value also decreased after six treatment methods.
The soil
nutrients after rice harvest showed that only the AP content did not
significantly differ during the treatments. The maximum nitrate N content was
7.978 mg/kg under the OPT-P, while the minimum was 2.623 mg/kg under the CON.
The content of ammonium N and OA had been improved after different
fertilization treatments. The highest AK content was 206.667 mg/kg under the
OPT-N, and the minimum value was 90.0 mg/kg under the CON. The pH decreased
after six treatment methods (Table 2).
Nutrient runoff loss under wheat and rice rotation
For the
nutrient runoff under the wheat cultivation, the TN and nitrate N considerably
varied, while the TP, ammonium N and total soluble phosphorus (TSP) showed the
minimal changes. The
proportion of lost nitrate N to total nitrogen were respectively 38.49, 57.30,
52.09, 55.05, 53.36 and 42.00% under the six treatments (Table 3). The TN, TP, nitrate N and TSP did not significantly
differ during among treatments, while the ammonium N loss under the OPT-NP+S
and OPT were significantly different. The highest mean of nutrient loss was 0.39 mg/L under
the OPT-NP+S, and the lowest value was 0.23 mg/L under the OPT. The ratios between ammonium N loss and TN among
treatment methods were 5.33, 4.30, 3.70, 4.95, 4.24 and 7.09%, respectively. The ratios between lost TSP under various treatments
and TP were 50.66, 54.10, 62.16, 53.075, 43.18 and 41.35%, respectively.
For the nutrient runoff under the rice cultivation,
the highest TN, TP, nitrate N, ammonium N and TSP were observed under the CON.
Only the average value of TN did not significantly differ during the
treatments. The proportions of lost nitrate N to TN under various treatments
were respectively 35.18, 32.11, 31.97, 17.10, 20.67 and 30.99%. The ratios between ammonium N loss and TN under
treatment methods were respectively 10.42, 8.64, 8.21, 8.50, 7.00 and 8.39%. The highest average loss was 0.216 mg/L under the CON
and the lowest loss was 0.116 mg/L under the OPT-P. The ratios between lost TSP and TP under various
treatments were 72.34, 81.2, 83.67, 63.18, 73.89 and 79.41% (Table 4).
Nutrient contents and yields of wheat and rice
plants
Table 1: Significance test
for soil nutrients among six treatments
under wheat cultivation
|
Nitrate
N (mg/kg) |
Ammonium N (mg/kg) |
OA (mg/kg) |
AP (mg/kg) |
AK (mg/kg) |
pH |
CK |
3.80 |
1.62a |
27.70b |
4.62b |
103.33c |
6.84a |
CON |
3.62 |
0.94b |
38.15a |
20.25a |
101.33c |
6.70b |
OPT |
3.58 |
0.68b |
38.94a |
20.37a |
160.00ab |
6.61c |
OPT-N |
3.70 |
2.12a |
36.27a |
22.42a |
180.00a |
6.58cd |
OPT-P |
3.10 |
1.45ab |
38.16a |
6.77b |
140.00b |
6.63bc |
OPT-NP+S |
3.15 |
1.28b |
40.68a |
7.08b |
163.33a |
6.53d |
Note: There are no significance for the values with the same letter in
each row (P < 0.05). OA, AP and AK denote organic matter, available
phosphorus and available potassium, respectively; CK, CON, OPT, OPT-N, OPT-P
and OPT-NP+S denote non-N-fertilised control, conventional N management based
on local custom, optimised N management, 30% reduced N compared to OPT, 50%
reduced P on the basis of OPT and straw with chemical fertilizer @200 kg of
wheat straw per acre on the basis of OPT-N and OPT-P
Table 2: Significance test
for soil nutrients among six treatments
under rice cultivation
|
Nitrate
N (mg/kg) |
Ammonium N (mg/kg) |
OA (mg/kg) |
AP (mg/kg) |
AK (mg/kg) |
pH |
CK |
5.42b |
1.36c |
21.55b |
15.51 |
103.33d |
7.10a |
CON |
2.62c |
2.67b |
28.21a |
15.92 |
90.00d |
6.72b |
OPT |
5.97b |
2.61b |
26.33ab |
20.64 |
163.33bc |
7.06ab |
OPT-N |
6.04b |
2.29b |
30.89a |
15.55 |
206.67a |
6.80b |
OPT-P |
7.98a |
2.06b |
26.52ab |
16.43 |
180.00b |
6.87b |
OPT-NP+S |
4.18b |
5.48a |
31.22a |
15.01 |
150.00c |
6.89ab |
Note: There are no significance for the values with the same letter in
each row (P < 0.05). OA, AP and AK denote organic matter, available
phosphorus and available potassium, respectively; CK, CON, OPT, OPT-N, OPT-P
and OPT-NP+S denote non-N-fertilised control, conventional N management based
on local custom, optimised N management, 30% reduced N compared to OPT, 50%
reduced P on the basis of OPT and straw with chemical fertilizer @200 kg of
wheat straw per acre on the basis of OPT-N and OPT-P
The mean values of TN and total potassium (TK) in wheat plants did not
significantly vary among treatments, while that of TP and crop yield
significantly differed among the six treatments. The TP content followed the
order of CK > CON > OPT-NP+S > OPT-N > OPT > OPT-P. The LSD test
revealed that wheat yield followed the order of OPT-P > OPT-N > OPT >
OPT-NP+S > CON > CK (Table 5).
Only the TK content did not significantly
differ for the six treatments. The TN content decreased after fertilization
treatments. There were significant differences for the other five treatments
except the CK. The TP content significantly differed between the six treatment
methods and followed the order of CON > CK >
OPT > OPT-N >OPT-NP+S>OPT-P. The rice
yield followed the order of OPT > OPT-NP+S > OPT-P >
OPT-N > CON >
CK (Table 6).
Discussion
Table
3: Significance test for
the wheat
runoff losses among six treatments (unit:
mg/L)
Table 5: Significance test for the wheat nutrients
and yield among six treatments
|
TN (%) |
TP (%) |
TK (%) |
Yield
(kg/ha) |
CK |
1.19 |
0.29a |
0.91 |
3684.41b |
CON |
0.84 |
0.17ab |
1.16 |
4567.77a |
OPT |
0.86 |
0.13b |
0.96 |
4925.04a |
OPT-N |
0.94 |
0.13b |
0.89 |
5087.41a |
OPT-P |
0.85 |
0.13b |
0.79 |
5154.87a |
OPT-NP+S |
0.84 |
0.14b |
1.08 |
4817.54a |
Note: There are no significance for the values with the same letter in each
row (P < 0.05). TN, TP and TK denote total nitrogen, total phosphorus
and total potassium, respectively; CK, CON, OPT, OPT-N, OPT-P and OPT-NP+S
denote non-N-fertilised control, conventional N management based on local
custom, optimised N management, 30% reduced N compared to OPT, 50% reduced P on
the basis of OPT and straw with chemical fertilizer @200 kg of wheat straw per
acre on the basis of OPT-N and OPT-P, respectively
Table 6: Significance test for the rice nutrients
and yield among six treatments
|
TN (%) |
TP (%) |
TK (%) |
Yield
(kg/ha) |
CK |
2.16a |
0.37ac |
1.11 |
5434.78d |
CON |
1.64b |
0.37ac |
1.10 |
8248.43c |
OPT |
1.36b |
0.34abc |
1.14 |
9532.68a |
OPT-N |
1.50b |
0.27abc |
1.24 |
8503.30c |
OPT-P |
1.48b |
0.20b |
1.10 |
8783.06b |
OPT-NP+S |
1.64b |
0.23b |
1.26 |
9272.86ab |
Note: There are no significance for the values with the same letter in each
row (P < 0.05). TN, TP and TK denote total nitrogen, total phosphorus
and total potassium, respectively; CK, CON, OPT, OPT-N, OPT-P and OPT-NP+S
denote non-N-fertilised control, conventional N management based on local
custom, optimised N management, 30% reduced N compared to OPT, 50% reduced P on
the basis of OPT and straw with chemical fertilizer @200 kg of wheat straw per
acre on the basis of OPT-N and OPT-P, respectively
|
TN |
TP |
Nitrate
N |
Ammonium N |
TSP |
CK |
5.82 |
0.30 |
2.24 |
0.31ab |
0.15 |
CON |
6.51 |
0.27 |
3.73 |
0.28ab |
0.15 |
OPT |
6.22 |
0.26 |
3.24 |
0.23b |
0.16 |
OPT-N |
5.45 |
0.23 |
3.00 |
0.27ab |
0.12 |
OPT-P |
6.84 |
0.26 |
3.65 |
0.29ab |
0.11 |
OPT-NP+S |
5.50 |
0.27 |
2.31 |
0.39a |
0.11 |
Note: There are no significance for the values with the same letter in
each row (P < 0.05). TN, TP and TSP denote total nitrogen, total
phosphorus and total soluble phosphorus, respectively; CK, CON, OPT, OPT-N,
OPT-P and OPT-NP+S denote non-N-fertilised control, conventional N management
based on local custom, optimised N management, 30% reduced N compared to OPT,
50% reduced P on the basis of OPT and straw with chemical fertilizer @200 kg of
wheat straw per acre on the basis of OPT-N and OPT-P, respectively
Table 4: Significance test for the rice
runoff losses among six treatments (unit: mg/L)
|
TN |
TP |
Nitrate
N |
Ammonium N |
TSP |
CK |
3.13 |
0.19ab |
1.12ab |
0.33ab |
0.14b |
CON |
4.64 |
0.27a |
1.49a |
0.40a |
0.22a |
OPT |
3.91 |
0.20ab |
1.25ab |
0.32ab |
0.16ab |
OPT-N |
3.86 |
0.24ab |
0.66b |
0.33ab |
0.15ab |
OPT-P |
3.87 |
0.16b |
0.80ab |
0.27b |
0.12b |
OPT-NP+S |
3.55 |
0.17b |
1.10ab |
0.30ab |
0.14b |
Note: There are no significance for the values with the same letter in
each row (P < 0.05). TN, TP and TSP denote total nitrogen, total
phosphorus and total soluble phosphorus, respectively; CK, CON, OPT, OPT-N,
OPT-P and OPT-NP+S denote non-N-fertilised control, conventional N management
based on local custom, optimised N management, 30% reduced N compared to OPT, 50%
reduced P on the basis of OPT and straw with chemical fertilizer @200 kg of
wheat straw per acre on the basis of OPT-N and OPT-P, respectively
The results
showed that fertilization can increase the soil OA content (Galantini and
Rosell 2006) and the accumulation
of OA can be significantly improved under the OPT-NP+S. Appropriate
reduction of N, P fertilizer and straw with chemical fertilizer could increase
ammonium N in rice soil. After chemical fertilizer
application, the soil available nutrients increased significantly (Moharana et al. 2012; Joshi et al. 2015),
while the soil pH decreased. It showed
that rational fertilization can reduce the pH of soil (Li et al.
2007, 2017). The AK content of wheat
and rice soils were the highest under the OPT-N and appropriate reduction of N
fertilizer could increase the soil AK content.
Through the
improvement of fertilization methods, the amount of N and P losses can be
effectively reduced (Zhao et al. 2006). The rate of nitrate N loss
in wheat under the CON was the largest and ammonium N loss under the OPT-NP+S
was the largest. The loss rate of TSP was the largest under the
OPT. The loss rate of nitrate N and ammonium N in rice
soil were the largest under the CON and the TSP showed the same trend under the
OPT. The runoff loss of N and P fertilizers has a
certain relationship with the rainfall situation and farmland farming
conditions. In addition, there are many other external
factors, which will inevitably cause certain errors during the testing process
(Li et al. 2017).
After
fertilization, the TP nutrient in wheat and rice plants was the least under the
OPT-P. Reducing the usage of P fertilizer will reduce the
absorption of P in plants. The uptake of N in rice
plants was reduced by fertilization. The
absorption of nutrients by crops mainly comes from soil and fertilization (Fageria et al.
2016). In terms of absorption,
more than two-thirds of the N, P and K at different growth stages are derived
from the soil, and most of them are obtained from the soil than from
the fertilizers (Smith 1976). Fertilization
treatments can increase the crop yield, but yields vary with different
fertilization treatments. The reason was that
different fertilization treatments have certain effects on soil fertility and
nutrient uptake by various plants (Mohammad et al. 2003).
Conclusion
The effects of different fertilisation treatments
under a rice-wheat rotation system revealed imbalances in different soil
nutrients. The order of TN loss in wheat among treatments was
OPT-P > CON > OPT > OPT-NP+S > OPT-N and that of TP loss was
CON>OPT-NP+S>OPT-P>OPT>OPT-N. For rice cultivation, the order of TN
loss was CON> OPT> OPT-P> OPT-N> OPT-NP+S and TP loss was CON >
OPT-N > OPT > OPT-NP+S> OPT-P. The
absorption of N, P and K nutrients in rice was slightly higher than wheat. The
wheat plant yield followed the order of OPT-P > OPT-N > OPT > OPT-NP+S
> CON > CK and that
for rice followed the order of OPT > OPT-NP+S > OPT-P > OPT-N > CON > CK.
Acknowledgements
The project was supported by National Key Research and Development Program
of China (2016YFD0800904), Natural Science Research Project of Anhui Provincial
Education Department (KJ2018A0009) and Anhui Provincial Science and Technology
Project (17030701062). We should be grateful to Professor Youhua Ma from Anhui
Agricultural University for the data support.
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