Cheng 2014
Cheng 2014
To cite this article: Dongdong Cheng, Yan Wang, Guizhe Zhao & Yaqing Liu (2014): Effects of Polymeric Slow
Release Fertilizer on Chinese Cabbage Growth and Soil Nutrients, Archives of Agronomy and Soil Science, DOI:
10.1080/03650340.2014.965695
Disclaimer: This is a version of an unedited manuscript that has been accepted for publication. As a service
to authors and researchers we are providing this version of the accepted manuscript (AM). Copyediting,
typesetting, and review of the resulting proof will be undertaken on this manuscript before final publication
of the Version of Record (VoR). During production and pre-press, errors may be discovered which could
affect the content, and all legal disclaimers that apply to the journal relate to this version also.
Taylor & Francis makes every effort to ensure the accuracy of all the information (the “Content”) contained
in the publications on our platform. However, Taylor & Francis, our agents, and our licensors make no
representations or warranties whatsoever as to the accuracy, completeness, or suitability for any purpose of
the Content. Any opinions and views expressed in this publication are the opinions and views of the authors,
and are not the views of or endorsed by Taylor & Francis. The accuracy of the Content should not be relied
upon and should be independently verified with primary sources of information. Taylor and Francis shall
not be liable for any losses, actions, claims, proceedings, demands, costs, expenses, damages, and other
liabilities whatsoever or howsoever caused arising directly or indirectly in connection with, in relation to or
arising out of the use of the Content.
This article may be used for research, teaching, and private study purposes. Any substantial or systematic
reproduction, redistribution, reselling, loan, sub-licensing, systematic supply, or distribution in any
form to anyone is expressly forbidden. Terms & Conditions of access and use can be found at http://
www.tandfonline.com/page/terms-and-conditions
Publisher: Taylor & Francis
DOI: 10.1080/03650340.2014.965695
Effects of Polymeric Slow Release Fertilizer on Chinese Cabbage Growth and Soil
Nutrients
t
ip
Dongdong Chenga,b, Yan Wanga, Guizhe Zhaoa, Yaqing Liua*
cr
Downloaded by [New York University] at 11:59 11 October 2014
us
a
Research Center for Engineering Technology of Polymeric Composites of Shanxi Province,
Abstract
ce
One pot experiment was conducted to study the effects of a new polymeric slow release
Ac
fertilizer (PRF) on Chinese cabbage growth and soil nutrients. The experiment comprised three
kinds of fertilizer (common compound fertilizer, 21% and 45% solubility of PRF in 25oC water,
all fertilizers with N:P2O5:K2O=10:5.7:20) and three fertilizer levels (0, 21.6, 43.2 g m-2).
Results showed that the high water-soluble PRFs (PRFHH and PRFHL) fit nutrient
requirements of Chinese cabbage and the high fertilization level significantly increased the
yield and improved quality of Chinese cabbage. Although the PRFHL treatment at 21.6 g
fertilizer m-2 had one-half less supplied nutrient than that of common compound fertilizer
treatment (43.2 g fertilizer m-2), the yield of Chinese cabbage with PRFHH and PRFHL was 8.0%
more. The soluble sugar, vitamin C and leaf chlorophyll contents of Chinese cabbage can be
effectively improved with PRFHH (43.2 g m-2), PRFHL (21.6 g m-2), and PRFLH (low
water-soluble PRF, 43.2 g m-2). The PRF treatment reduced the nitrate content and improved
soil capacity of supplying nutrient effectively, and there were no changes in values of pH and
t
ip
Keywords: polymer, slow release fertilizer, Chinese cabbage, quality, soil nutrient
cr
Downloaded by [New York University] at 11:59 11 October 2014
Introduction
us
In the past few decades, there was a significant increase in fertilizer consumption (Ju et al.
an
2004). Currently, the excessive use of fertilizers in China has caused environmental damage,
especially non-point source pollution (Zhang and Wang 2002; Jin et al. 2005). Fertilizer applied
M
in intensive farming systems in China has increased significantly, such as greenhouse vegetable
production systems (Cakmak 2002). The farmers increased production to obtain higher
d
economic value of the extra yields by large amounts of fertilizer and water measures because
e
the absorption ability of water and fertilizer is weak. For example, fertilizer N is often applied at
pt
a rate more than 1200 kg N ha-1 and irrigation water in 1000 mm crop-1 in Shouguang Shandong
ce
province, North China (Zhu et al. 2005; Zhang et al. 1996; Zhang et al. 2005). The high inputs
and low crop recoveries of fertilizer nutrients resulted in a significant increase of NO3--N in the
Ac
surface soil and groundwater systems (Sainju et al. 2001; Zhang et al. 1996; Yu et al. 2006; Ju et
al. 2007).
For these reasons, great attention has been given to find new types of fertilizers that, ideally,
should be low in cost with less application amounts and high nutrient use efficiency. The
slow/controlled release fertilizers possess a great potential for enhancing fertilizer efficiency
and reducing environment pollution (Shoji and Kanno 1994; Shaviv and Mikkelsen 1993).
Several slow and controlled release fertilizers have been developed during the past 50 years,
including sulfur coated urea (SCU), urea formaldehyde (UF), and resin-coated urea (CRU).
Although all of these slow and controlled released fertilizers can improve the efficiency of the
fertilizer to some extent, but the high cost prevents their extensive application in agricultural
fields, except for certain nursery plants (Shaviv and Mikkelsen 1993; Bansiwal et al. 2006).
Besides, the residual membrane shell of resin-coated CRU cannot be degraded by microbial in
t
ip
short-term, which may lead to the destruction of soil after long-term application of resin-coated
cr
fertilizer
Downloaded by [New York University] at 11:59 11 October 2014
A new slow release fertilizer product was synthesized in our laboratory, currently named as
us
polymeric slow release fertilizer (PRF). The PRF was synthesized through cross-linking
an
reaction and has slight solubility in water. Under the impact of enzymes and microorganisms in
soil, the nutrient was released when molecular chain of PRF was destroyed (CN Patent:
M
201010518088.8). In order to discover the effects of different water-soluble PRFs on vegetable
growth and nutrient absorption, we conducted for a pot experiment with Chinese cabbage as a
d
research crop.
e
pt
34.74 g of 37% (w/w) formaldehyde solution and 54 mL of distilled water were placed into a
Ac
glass flask and stirred with 21.41 g of urea. 5% KOH solution was added to the above solution
to adjust the pH 8.0, and the flask was placed in a water bath at 25 oC for 2 h with stirring. And
then, 10.92 g of KH2PO4 (33.33 wt% water solution) and 30.04 g of K2SO4 were slowly added
into the above mixture. After being stirred for 40 min at 80 oC, the mixture was transferred to a
beaker in an oven at 100 °C for 3 h till the reaction completed, and then dried in an oven at 55 °C
until the weight was constant. The product was a white powder, and the average molecular
weight was 10,790 g mol-1.
The experiment was performed at the Research Center for Engineering Technology of
Polymeric Composites of Shanxi Province, North University of China to investigate the effects
of a new PRF on Chinese cabbage (local name: Shanghai Green) Brassica chinensis L.
campestris growth and soil nutrients under natural conditions. The annual rainfall and air
t
ip
temperature are 431.0 mm and 10 °C, respectively. The properties of soil were analyzed
cr
according to standard methods (Lu 2000). Soil pH, EC, available N, available P (extractant 0.5
Downloaded by [New York University] at 11:59 11 October 2014
moL L-1 NaHCO3) and K (extractant 1 moL L-1 NH4OAc) were 8.22, 133.20 μS cm-1, 34.96,
us
11.92 and 73.50 mg kg-1, respectively. The texture of soil was silt loam (12.0% clay, 38.0% sand,
an
and 50.0% silt contents), which was measured using micro-pipette method (Lu 2000). The
PRFs used in this study contains two types, which were low water-soluble of 21% and high
M
water-soluble of 45% in 25°C water (1:20 w/v). All PRF was produced by the Research Center
The N, P, K and S contents of the PRF are 10.0%, 2.5%, 18.6%, and 4.4%), respectively. The
e
common inorganic compound fertilizer contains 10% N, 2.5% P, 18.6% K, 4.4% S (Common
pt
inorganic compound fertilizer was mixed by 21.41 g urea, 10.92 g KH2PO4, 30.04 g K2SO4 and
ce
Two days before sowing, all fertilizer treatment boxes (length × width × height=120 × 42 × 28
Ac
cm) were supplied with fertilizer, and the upper and lower soil was mixed, the layer thickness
was 25 cm. For each box, 4 g of Chinese cabbage seeds was uniformly sown in the box, and
then cover 2-3 cm deep soil on July 5, 2012 and 2013. After emergence, 15 plants were kept in
every box. Every box was introduced with 15 L of water every 2 d. Cabbage was harvested on
August 24, 2012 and 2013, and about 500 g soil samples from 0-20 cm layer were collected by
designed as a completely randomized block with three replicates and seven treatments:
- CK (no fertilizer),
t
ip
- PRFLL (low water-soluble polymeric slow release fertilizer, 21.6 g m-2),
cr
- PRFHH (high water-soluble polymeric slow release fertilizer, 43.2 g m-2),
Downloaded by [New York University] at 11:59 11 October 2014
us
an
Analysis of soil chemical properties
Soil inorganic nitrogen (NH4+-N and NO3--N, extraction with 0.01 mol L-1 CaCl2)
M
concentration was analyzed by AA3-A001-02E Auto-analyzer (Bran-Luebbe, Norderstedt,
Instrument Co., Shanghai, China) and EC Meter (DDS-307, Precision Scientific Instrument Co.,
e
Shanghai, China). The contents of available P (0.5 moL L-1 NaHCO3 leaching) and K (1 moL
pt
L-1 NH4OAc extraction) were determined by Mo-Sb colorimetry and flame photometry (FP640,
ce
At harvest, all cabbages of each plot were individually weighed and washed with deinoized
water, and 500 g was oven dried at 80oC for determination of dry mass and N, P, K contents.
Chlorophyll a and b contents were determined by acetone extraction method (Zhao, 2002).
Vitamin C (VC) in the cabbage was analyzed in fresh plant samples (Lu 2000). Soluble sugar
and nitrate contents were determined as the method described by Chen et al. (2004). After the
dry cabbage was collected, the dried plant material was ground so as to pass through a 2.0 mm
stainless screen in a Wiley mill, and the sample was decomposed by sulfuric acid/H2O2 method.
The N was analyzed by Kjeldahl method, P and K by Mo-Sb colorimetry and flame photometry
The nutrient use efficiency (NUE) was calculated according to Equation (1):
t
ip
Where: Y-the yield of cabbage; C-the content of nutrient in the plant; x-treatment with
cr
fertilizing; 0-control treatment with no fertilizing; F-the nutrient content of fertilizer.
Downloaded by [New York University] at 11:59 11 October 2014
Statistical analysis
us
Statistical analysis on the difference between the means of treatments was conducted using SAS
an
program (Hu 2010).
M
Results and discussion
For the four treatments fertilized with common compound fertilizer and high water-soluble PRF,
e
the soil available N content was significantly higher than that without fertilizer (Table 1). The
pt
contents of available P in the soil of PRFLH, PRFLL, PRFHH treatments were significantly
ce
higher than CCFH, CCFL, PRFLL and control treatment. In addition, the content of soil
available P was similar between the common compound fertilizer and low water-soluble PRF
Ac
treatments, which was due to the less release of P from PRF and the P fixation of the common
compound fertilizer in the soil. Different fertilizer treatments also resulted in significant
differences in soil available K content. The highest available K content was found in PRFLH,
followed by PRFHH, CCFH, PRFHL, PRFLL, CCFL, and the control, which indicated that low
water-soluble PRF was useful for retarding the K release. The K release rate of PRF is
controlled by the solubility of PRF, and there was a negative correlation between the solubility
and the molecular weight of PRF (Cheng 2013). So, compared with the high water-soluble PRF,
more K from the low water-soluble PRF was kept in the frequently irrigated soil in the short
term. For common fertilizer, K is completely dissolved and could not be stored in the soil with
low clay content for a long time. Compared with the control, soil EC was not significantly
changed with the addition of various fertilizers. At the common compound fertilizer application
rate of 43.2 g m-2, soil pH increased significantly, but the addition of PRF could not
t
ip
significantly change the pH of soil.
cr
PRF is a chemically degradable material with low solubility that would gradually decompose in
Downloaded by [New York University] at 11:59 11 October 2014
soil (Zhao et al. 2010). The nutrient release cycle was determined by the solubility of fertilizer,
us
the low water solubility of PRF has a longer term than high water solubility, which contained
an
more amount of relative small molecules that can be degraded by soil microbial and enzyme in
short term (Cheng et al. 2013). At harvest, the available N, P, K of soil treated with high
M
water-soluble PRF were higher than that with low water-soluble PRF, which was due to the
released amount of nutrients. It could be found that the amounts of N, P, K absorbed by Chinese
d
treatments with high water-soluble PRF compared to low water-soluble PRF (Table 5). Besides,
pt
for the treatment of common compound fertilizer, the available N content in the soil was
ce
significantly higher than that of low water-soluble PRF. For N uptake, the common compound
fertilizer showed 23%~26% higher amounts than low water-soluble PRF. One possible
Ac
explanation of the result is that the N release in low water-soluble PRF was slower than that of
common compound fertilizer, considering the fact that most available N is absorbed by plant
and existed in the soil in small amounts. The highest pH of soil was observed with the CCFH
treatment, because large amounts of NH4+ are absorbed by soil particles. On the contrary,
slowly released NH4+ from PRF seemed to be absorbed mainly by the growing plant and only a
small amount remained in the soil, so the pH of PRF treatment cannot be changed significantly.
Table 1
Chlorophyll contents
Chlorophyll is composed of carbon, hydrogen, oxygen, and nitrogen elements, and plays an
important role in nitrogen metabolism and carbon dioxide fixation in plants. Consequently, the
chlorophyll content can indirectly demonstrate soil N-supplying capacity and have long been
suggested as an index of the productive capacity of crop species (Ogunlela et al. 1989; Li et al.
t
ip
2013). In our study, it was found that fertilizer types affected chlorophyll differently (Table 2).
cr
Compared to that without fertilizer control (CK), the other fertilization treatments variously
Downloaded by [New York University] at 11:59 11 October 2014
increased the chlorophyll a content of Chinese cabbage by a certain extent, except for the low
us
amount of low water-soluble PRF treatment (PRFLL). At harvest time, the chlorophyll a
an
content was increased by 1.0-25.7% in dependence of fertilizer treatments compared to control.
common compound fertilizer treatments (CCFH, CCFL) and high amount of high
d
water-soluble PRF treatment (PRFHH) were higher than in the control without fertilizer. The
e
treatments with common compound fertilizer and high water-soluble PRF had a positive effect
pt
on total chlorophyll content compared to low water-soluble PRF treatment. Besides, a similar
ce
observation was obtained on soil nutrient contents due to the effects of different fertilizer
treatments (Table 1). The available N content of soil from the high water-soluble release
Ac
fertilizer was higher than that from the low water-soluble slow release fertilizer, so more N was
provided to the plant growth and promotion of chlorophyll synthesis. This indicates that the low
water-soluble slow release fertilizer released less amounts of nutrient in short term and cannot
meet the requirements of Chinese cabbage, and the high water-soluble release fertilizer could
Table 2
Cabbage yield and economic benefits
Different fertilizers had obvious effects on Chinese cabbage yields (Table 3). The control (CK)
had the lowest yield, only 3.10 kg m-2, due to absence of fertilizer application, followed by
CCFL, in which only half amount of fertilizers was applied. Among the other five treatments,
the PRFHH treatment produced the highest yield, followed by PRFHL, CCFH, PRFLH, and
PRFLL. Compared to the conventional fertilizer with the same amount of nutrients applied
t
ip
higher yields could be achieved when high water-soluble PRF was used, the difference was
cr
statistically significant. In addition, the treatment with low amount of high water-soluble
Downloaded by [New York University] at 11:59 11 October 2014
release fertilizer had a higher yield than CCFH treatment even though only half of nutrient
us
amounts were used. Besides, it could be found that N, P, K use efficiencies were 2.8%, 54.4%,
an
47.4%, respectively, higher in the PRFHL than CCFH treatments. This could be assumed due to
the improvement of nutrient utilization efficiency of Chinese cabbage and the reduction of
M
fertilizer loss in the presence of PRF. The price of Chinese cabbage was 2 Yuan (RMB) kg-1 in
China in 2013. It can be found that the net income and the ratio of output to input were 32% and
d
48%, respectively, higher in the PRFHH than the common inorganic fertilizer (CCFHH)
e
treatments and the ratio of output to input of high water-soluble PRF was higher than those of
pt
low water-soluble PRF (Table 3). All these showed that the high water-soluble PRF can
ce
Table 3
Ac
Cabbage quality
Treatments affected soluble sugars, Vitamin C, and NO3--N contents (Table 4). Compared to the
CK treatments, fertilization with PRFLH, PRFHH, and PRFHL significantly enhanced the
soluble sugar content. The treatments of PRFLH and PRFHL greatly increased the soluble
sugar content, up to 21.86 and 25.60 mg g-1, respectively. Vitamin C (VC) is regarded as one of
the important nutritive qualities of vegetables. In the experiment, the highest VC content was
achieved when PRFLH was applied, followed by PRFLL. Statistically the lowest VC levels
occurred with CK, CCFH, and PRFHH treatments. Nitrate was one important factor, which can
limit safe quality of vegetables and hinder human health (Yousif et al. 2010). The U.S.
Environmental Protection Agency (EPA) reference dose for nitrate is equivalent to about 7.0
mg kg-1 body weight per day (Mensinga et al. 2003). A person weighing 60 kg, as
recommended by the U.S. Environmental Protection Agency, consumed this item would not
t
ip
exceed 420 mg per day. Because nitrate will be leached about 50% when cabbage is cooked, so
cr
the limited amount of nitrate is 840 mg. Assuming that everyone takes 500 g of vegetable every
Downloaded by [New York University] at 11:59 11 October 2014
day, the most allowable concentration of nitrate in the vegetable is 1680 mg kg-1. The maximum
us
of nitrate in vegetables is 1440 mg kg-1 according to the Standardization Administration of the
an
People’s Republic of China (GB/T 19338-2003). The results showed that the CCFHH, CCFHL
treatments had a high level NO3- content, up to 2211 and1534 mg kg-1, respectively. Application
M
of PRF decreased NO3--N content of Chinese cabbage. The nutrients in PRF were released
slowly and well consistent with the plant absorption. It could be attributed to the improved
d
nitrogen quantity, which could increase the absorption of nitrate and result in less nitrate
e
In well aerated soils, urea from common compound fertilizer is rapidly hydrolyzed to NH4+
ce
which is thereafter converted in NO3- (Rodrigues et al. 2004). Thus, in PRF treatments, NH4+
and/or NO3- were available for plant uptake. Qiu et al. (2013) showed that the usage of slow
Ac
release fertilizer decreased the content of NO3--N and increased VC and soluble sugar contents
in the Chinese cabbage compared to common compound fertilizer. The results from Cao et al.
(2006) also showed that the application of controlled release fertilizer could increase VC by
12.5%.
Table 4
Nutrient uptake
The effect of treatments on plant N, P, and K uptake was significant (Table 5). At all applied
nutrient levels plant nutrient uptake was higher at the application rate of 43.2 g m-2 compared to
the low rate of 21.6 g m-2. The uptake of K at 43.2 g fertilizer m-2 was not significantly different
from those of 21.6 g fertilizer m-2. The results from nutrient uptake showed that the high
compound fertilizer treatment, the maximum uptake of N, P, and K increased by 13.9, 22.0, and
t
ip
22.9%, respectively, in treatments with PRFs (Table 5). This was because the PRF has the
cr
capacity of continuous and sustainable supply of nutrients during the whole vegetation period.
Downloaded by [New York University] at 11:59 11 October 2014
As opposed to that, common compound fertilizer released numerous nutrients at the beginning
us
of the vegetation, and most of available N, P, K could not immediately be used by plant, H2PO4-
an
and K+ could be fixed and adsorbed by soil, and a part of N could be volatilized in the form of
ammonia (Li et al. 2014). The remaining nutrient amounts were not able to supply such amount
M
of nutrients as high water-soluble PRF.
Table 5
e d
Conclusions
pt
In the light of two-years’ results, it can be concluded that the application of PRF can effectively
ce
improve soil capacity of supplying nutrient, and did not change the soil pH and EC. High
water-soluble PRF can improve quality and increase both the plant growth and fruit yield of
Ac
Chinese cabbage. Compared to the common compound fertilizer treatment of 43.2 g m-2, the
high water-soluble PRF treatment at 21.6 g m-2 could increase the yield 8%. Although the use of
low water-soluble PRF did not significantly enhance the yield, the use of low water-soluble
Acknowledgments
This work was supported by the project of Technology promotion of Shanxi Province (No
20130311009-6); The Graduate Innovation of Shanxi Province (No 20123094); and The
References
Bansiwal AK, Rayalu SS, Labhasetwar NK, Juwarkar AA, Devotta S. 2006.
t
ip
Surfactant-modified zeolite as a slow release fertilizer for phosphorus. J Agric Food
cr
Chem. 54:4773-4779.
Downloaded by [New York University] at 11:59 11 October 2014
Bao SD. 2000. Agricultural Chemistry Analysis of Soil. Beijing, China: China Agriculture
us
Press; p. 32-156. an
Cakmak I. 2002. Plant nutrition research: Priorities to meet human needs for food in sustainable
fertilizer types on yield, N uptake, and quality of Chinese cabbage (in Chinese). Acta
d
Chen BM, Wang ZH, Li SX, Wang GX, Song HX, Wang XN. 2004. Effects of nitrate supply on
pt
plant growth, nitrate accumulation, metabolic nitrate concentration and nitrate reductase
ce
Cheng DD, Zhao GZ, Liu YQ, Hao SQ. 2013. Influences of Soil Temperature and Moisture on
Ac
Nutrients Release of Polymeric Slow Release Fertilizer and Soil Enzyme Activity (in
Hu LP. 2010. SAS Statistical Analysis TutorialBeijing, China: Electronic Industry Press; p.
56-93.
Jin XC, Xu QJ, Huang CZ. 2005. Current status and future tendency of lake eutrophication in
Ju XT, Liu XJ, Zhang FS. 2004. Nitrogen fertilization, soil nitrate accumulation, and policy
Li J, Shi YL, Luo JF, Houlbrooke D, Ledgard S, Ghani A, Lindsey S. 2014. Effects of form of
t
ip
effluent, season and urease inhibitor on ammonia volatilization from dairy farm effluent
cr
applied to pasture. J. Soil. Sediment. 14: 1341-1349.
Downloaded by [New York University] at 11:59 11 October 2014
Li Y, Zou YN, Wu QS. 2013. Effects of Diversispora spurca inoculation on growth, root system
us
architecture and chlorophyll contents of four citrus genotypes. Int J Agric Biol.
an
15:342-346.
Lu RK. 2000. The analytical methods for soil and agrochemistry. Beijing, China: Agricultural
M
Science and Technology Press; p. 220-245.
Ogunlela VB, Kullmann A, Geisler G. 1989. Leaf Growth and Chlorophyll Content of Oilseed
pt
Rape (Brassica napus L.) as Influenced by Nitrogen Supply. J Agron Crop Sci. 2:73-89.
ce
Qiu XK, Wang YH, Hu GQ, Wang QH, Zhang XW, Dong YJ. 2013. Effect of different
Rodrigues MA. 2004. An in situ incubation technique to measure the contribution of organic
Sainju UM, Singh BP, Whitehead WF. 2001. Comparison of the effects of cover crops and
nitrogen fertilizer on tomato yield, root growth, and soil properties. Sci Hortic.
91:201-214.
Shaviv A, Mikkelsen RL. 1993. Controlled-release fertilizers to increase efficiency of nutrient
Shoji S, Kanno H. 1994. Use of polyolefin-coated fertilizers for increasing fertilizer efficiency
and reducing nitrate leaching and nitrous oxide emissions. Nutr Cycl Agroecosys.
39:147-152.
Standard No: GB 19338-2003. Tolerance limit for nitrate in vegetables. Beijing, China: China
t
ip
Standard Press.
cr
Yousif BS, Nguyen NT, Yasuko F. 2010. Effect of salinity on growth, mineral composition,
Downloaded by [New York University] at 11:59 11 October 2014
photosynthesis and water relations of two vegetable crops: New Zealand spinach
us
(Tetragonia tetragonioides) and water spinach (Ipomoea aquatica). Int J Agric Biol.
an
12:211-216.
Yu HM, Li ZZ, Gong YS, Mack U, Feger KH, Stahr K. 2006. Water drainage and nitrate
M
leaching under traditional and improved management of vegetable-cropping systems in
Zhang GH, Yuan LP, Guo YH, Zhu X, Zhang ZX. 2005. Effects of fertilization levels on the
e
growth and development of tomato in solar greenhouse. Trans Chin Soc Agric Eng.
pt
21:151-154.
ce
Zhang W, Wang XJ. 2002. Modeling for point-non-point source effluent trading: perspective of
Zhang WL, Tian ZX, Zhang N, Li XQ. 1996. Nitrate pollution of groundwater in northern
Zhao GZ, Liu YQ, Tian Y, Sun YY, Cao Y. 2010. Preparation and properties of macromelecular
17:119-125.
Zhao SJ. 2002. Techniques of plant physiological experiment. Beijing, China: China
Agricultural Science and Technology Press; p. 36-49.
Zhu JH, Li XL, Christie P, Li JL. 2005. Environmental implications of low nitrogen use
Zhu Q, Zhang M, Ma Q. 2012. Copper-based foliar fertilizer and controlled release urea
improved soil chemical properties, plant growth and yield of tomato. Sci
t
ip
Hortic-Amsterdam. 16:109-114.
cr
Downloaded by [New York University] at 11:59 11 October 2014
us
Treatment Available N Available P Available K pH EC
(mg kg-1) (μS cm-1)
CK 33.55 c 11.81 cd 70.00 f 8.23 b 121.23 a
an
Common fertilizer
CCFH 47.13 a 13.50 cd 90.00 bc 8.36 a 136.23 a
M
CCFL 49.41 a 11.58 cd 75.00 ef 8.29 b 134.57 a
Note: The data in the table are the average values of 2012 and 2013. Different letters within the same column indicate
differences at the 0.05 significance level.
Ac
Table 2: Effects of different fertilizer treatments on chlorophyll content.
Treatment Chlorophyll a Chlorophyll b Total Chlorophyll
(μg g-1)
CK 0.70 dc 0.24 b 0.94 c
Common fertilizer
CCFH 0.88 a 0.31 a 1.20 ab
CCFL 0.91 a 0.32 a 1.23 a
t
PRFLH 0.80 abc 0.26 b 1.06 bc
ip
PRFLL 0.71 d 0.24 b 0.95 c
cr
High water soluble fertilizer
Downloaded by [New York University] at 11:59 11 October 2014
us
PRFHL 0.85 ab 0.26 b 1.11 ab
Note: The data in the table are the average values of 2012 and 2013. Different letters within the same column indicate
differences at the 0.05 significance level.
an
M
e d
pt
ce
Ac
Table 3: Effects of different fertilizer treatments on yield and economic benefits of Chinese cabbage.
Treatments Fresh yield Rate of fertilizer application Fertilizer price Fertilizer cost Output value (Yuan Net income (Yuan The ratio of
(kg m-2) (×10-3 kg m-2) (Yuan (RMB) (×10-3 Yuan (RMB) m-2) (RMB) m-2) output to input
t
kg-1) (RMB) m-2)
rip
Downloaded by [New York University] at 11:59 11 October 2014
sc
Common fertilizer
CCFH 5.51 c 43.2 2.033 87.8 11.02 10.93 53.67
u
CCFL 3.82 e 21.6 2.033 43.9 7.64 7.60 7.55
an
Low water soluble fertilizer
PRFLH 4.36 d 43.2 2.406 103.9 8.72 8.61 23.06
M
PRFLL 4.18 d 21.6 2.406 52.0 8.36 8.31 40.15
(mg g-1)
CK 16.43 c 253 c 284 c 667 c
Common fertilizer
CCFH 17.06 c 298 bc 2211 a 880 a
CCFL 18.24 bc 323 abc 1534 b 814 a
t
Low water soluble fertilizer
ip
PRFLH 21.86 ab 417 a 598 c 762 b
PRFLL 17.31 c 408 a 377 c 658 c
cr
Downloaded by [New York University] at 11:59 11 October 2014
us
PRFHH 18.70 bc 259 c 558 c 701 b
PRFHL 25.60 a 387 ab 441 c 578 d
Note: The data in the table are the average values of 2012 and 2013. Different letters within the same column indicate
differences at the 0.05 significance level.
an
M
e d
pt
ce
Ac
Table 5. Effects of different fertilizer on Chinese cabbage N, P, K tissue content and nutrient
uptake.
Treatment Nutrient content (%) Nutrient uptake (g m-2)
N P K N P K
CK 1.81 c 0.46 c 3.08 a 4.10 e 1.04 e 6.96 d
Common fertilizer
CCFH 1.82 d 0.55 ab 3.35 a 8.90 b 2.18 b 13.3 abc
CCFL 1.59 d 0.54 ab 3.41 a 6.76 c 1.40 d 9.70 cd
t
Low water soluble fertilizer
ip
PRFLH 1.63 d 0.59 a 3.57 a 6.60 c 2.36 b 12.26 bc
PRFLL 1.59 c 0.57 a 2.94 a 5.46 d 1.96 c 11.88 bc
cr
Downloaded by [New York University] at 11:59 11 October 2014
us
PRFHH 2.67 a 0.55 ab 3.35 a 10.14 a 2.66 a 16.34 a
PRFHL 2.42 b 0.51 b 3.54 a 6.64 c 2.30 b 14.54 ab
Note: The data in the table are the average values of 2012 and 2013. Different letters within the same column indicate
differences at the 0.05 significance level.
an
M
e d
pt
ce
Ac