Bio-based Large Tablet Controlled-Release Urea: Synthesis

The top photo showed the actual sizes of LTCRU at these stages: (a) initial dissolution stage (from 0th to 3rd day, no volume change), (b) fast dissol...
0 downloads 0 Views 3MB Size
Full text access provided via ACS AuthorChoice

Agricultural and Environmental Chemistry

Bio-based Large Tablet Controlled-Release Urea: Synthesis, Characterization, and Controlled-Released Mechanisms Lu Liu, Tianlin Shen, Yuechao Yang, Bin Gao, Yuncong C. Li, Jiazhuo Xie, Yafu Tang, Shugang Zhang, Zhonghua Wang, and Jianqiu Chen J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.8b04042 • Publication Date (Web): 20 Sep 2018 Downloaded from http://pubs.acs.org on October 4, 2018

Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.

is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.

Page 1 of 30

Journal of Agricultural and Food Chemistry

1

Title

2

Bio-based Large Tablet Controlled-Release Urea: Synthesis, Characterization, and

3

Controlled-Released Mechanisms

4

Authors:

5

Lu Liua,+, Tianlin Shena,+, Yuechao Yanga,c,*, Bin Gaob, Yuncong C. Lic, Jiazhuo Xiea, Yafu

6

Tanga, Shugang Zhanga, Zhonghua Wanga, Jianqiu Chend

7 8

Affiliations:

9

a

National Engineering Laboratory for Efficient Utilization of Soil and Fertilizer Resources;

10

National Engineering & Technology Research Center for Slow and Controlled Release

11

Fertilizers, College of Resources and Environment, Shandong Agricultural University, Taian,

12

Shandong 271018, China

13

b

14

University of Florida, Gainesville, FL 32611, USA

15

c

16

University of Florida, Homestead, FL 33031, USA

17

d

18

Engineering Group Co., Ltd, Linshu, Shandong 276700, China

19

+

Agricultural and Biological Engineering, Institute of Food and Agricultural Sciences (IFAS),

Department of Soil and Water Science, Tropical Research and Education Center, IFAS,

State Key Laboratory of Nutrition Resources Integrated Utilization, Kingenta Ecological

Lu Liu and Tianlin Shen contributed equally to this work.

20 21

*

22

Yuechao Yang

23

Phone: 86-538-8242215

24

E-mail: [email protected].

Corresponding author

25

1 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

26

ABSTRACT

27

To improve nitrogen (N) use efficiency and minimize environmental pollution caused by

28

fertilizer over use, novel bio-based large tablet controlled-release urea (LTCRU) was prepared

29

by using bio-based coating materials to coat large tablet urea (LTU) derived from urea prills

30

(U). Nano fumed silica (NFS) was added to the bio-based coating materials to improve the

31

slow-release properties. Surface area of the LTU and U was measured by three-dimension

32

scanning. Compared with U, LTU had smaller surface area-to-weight ratio, which can reduce

33

the coating materials. Scanning electron microscope analysis showed that the addition of NFS

34

in bio-based coating materials reduced the porosity of the coating shells of LTCRUs and thus

35

enhanced the N release longevity of the controlled-released fertilizer. Depending on the pores

36

on the coating shells of LTCRU, two N release patterns were revealed. Because of the good

37

release characteristics, the novel LTCRU shows great potential to support sustainable

38

agricultural production.

39

KEYWORDS: Modified large tablet controlled-release urea; Surface area; Bio-based

40

material; Nano fumed silica; Release rate

2 ACS Paragon Plus Environment

Page 2 of 30

Page 3 of 30

Journal of Agricultural and Food Chemistry

41

INTRODUCTION

42

With rapid growth of global populations, agricultural production is requiring more and

43

more fertilizers to meet the demand for food.1 Nitrogen (N) fertilizers, especially urea, should

44

be applied in a controlled-release manner to increase their efficiency as well as to prevent

45

their loss via ammonia volatilization and leaching for soil and water pollution.2

46

Controlled-release urea (CRU) fertilizer can enhance crop yield and nutrient use efficiency

47

(NUE) with lower environment impact in comparison with the traditional N fertilizers.3-6

48

However, the high cost of coating materials of CRU and complicated production procedure

49

have limited their larger scale application in agricultural fields. In addition, most of the

50

coating materials are derived from petroleum resources which are expensive and

51

non-renewable. The coating shells may present potential risks to pollute the soil environment

52

after the nutrients are released from CRUs.7-8

53

Another method to improve the NUE is the use of urea super granules (USG), invented by

54

the International Fertilizer Development Center.9 Several studies have shown that the use of

55

USGs can not only reduce the ammonia volatilization losses but also reduce the usage of

56

fertilizer in the fields compared to the traditional fertilizer.10-11 However, USG without

57

coating must be placed deeply to avoid the burn of seeds or plant roots and ammonia

58

volatilization by fast dissolving in paddy soil. The deep placement method of the USG is

59

labor intensive and time consuming which has limited it used in large-scale agricultural

60

production systems.12 To solve these problems, novel large tablet polymer-coated urea

61

(LTPCU) has been produced by using the bio-based coating materials to coat on the surface

62

of LTU. Compared to normal CRU (diameter of 2-4 mm), LTPCU is more effective to save

63

the production cost by decreasing the usage of coating material.13 Therefore, LTPCU is more

64

suitable to be used in the agricultural production system.

65

Many types of materials have been used as coatings for CRU,14 including sulfur,15

3 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

66

petroleum based polymers such as polyurethane (PU),16 and bio-based polymers derived from

67

starch,17 cellulose,18-19 and vegetable oil.20 Castor oil could be used as the bio-polyol to

68

produce polyurethane without further treatments because of its high hydroxyl value. The use

69

of bio-based polymers as the coating for CRU has attracted much research attention recently

70

because they are more environmentally friendly than petrochemicals.21 However, most of the

71

bio-based coating materials are hydrophilic and the nutrient controlled release longevity is

72

hard to over 30 days of the bio-based CRUs.22 With the development of polymer technology,

73

it is possible to use some new modification technologies (nano materials, hydrophobic organ

74

silicon compounds) for the bio-based coating to improve the nutrient release characteristics of

75

bio-based CRU.23-25 In addition, research efforts have been made in understanding CRU’s

76

controlled-release process and behavior. The governing release characteristics and

77

mechanisms of CRU have been proposed and tested in previous studies. Findings from those

78

studies have suggested that the release of CRU is governed by simultaneous transport of both

79

liquid and vapor water between the inside and outside of the coating.26-27 The cracks and

80

micro pores existing on coatings are the main tunnels for the release.14 Controlled-release

81

systems have been developed and often used as mimics to study and evaluate the

82

controlled-release characteristics of CRUs. However, how much the modified bio-based

83

coating shells can influence the nutrient release characteristics, and what are the nutrient

84

release mechanisms of the modified large tablet controlled-release urea (MLTCRU) have not

85

been established and evaluated in previous studies.

86

The objective of this study was to prepare and evaluate the MLTCRU. Large tablet urea

87

(LTU) was first produced from urea powder with a tablet machine. Bio-based coating

88

materials derived from castor oil modified with nano fumed silica were then coated on the

89

LTU surface at different loadings to obtain the MLTCRUs. The differences between the

90

coatings of LTCRU and MLTCRU were characterized by SEM and FTIR. The nutrient

4 ACS Paragon Plus Environment

Page 4 of 30

Page 5 of 30

Journal of Agricultural and Food Chemistry

91

release characteristics of LTCRU and MLTCRU were evaluated with a laboratory

92

controlled-release system to quantify the release pattern as a function of volume change and N

93

release rate. The ultimate goal of this study is to develop a high efficiency and

94

environmentally friendly fertilizer.

95

EXPERIMENTAL SECTION

96

Materials. Urea prills (particle size of 0.5-2 mm with 46.2% N) were purchased from Luxi

97

Chemical Co., Ltd (Shandong, China). Methylene diphenyl diisocyanate (MDI) with 30.03

98

wt. % NCO group were obtained from Yantai Wanhua Polyurethane Co., Ltd. (Shandong,

99

China). Bio-polyol produced from castor oil and NFS was purchased from Aladdin Industrial

100

Co., Ltd. (Shanghai, China). Previous studies demonstrated that bio-polyol derived from

101

castor oil is biodegradable.28-31 With high hydroxyl value of 137.81±0.58 mg KOH/g, castor

102

oil is an ideal bio-based coating material. All the chemical agents were analytical grade and

103

used directly as received. Deionized water was used throughout the experiment.

104

Preparation of LTU. The LTUs were prepared from conventional urea prills. The urea

105

prills were mechanically molded into LTU using an extruder (YST-100T, Changzhou Jiuyajiu

106

Machinery Manufacturing Co. Ltd., China) under the pressure of 10 T (Ton). The height and

107

diameter of each tablet was 11.20 mm and 16.00 mm. The mass of each LTU was around

108

1.85-2.15 g and the N content of each LTU was about 0.85-0.99 g. The volume and surface

109

area of LTU were determined using the three-dimensional scanning technology with a laser

110

scanner (SLP-250, Wuxi SGKs Measurement Technology Co., Ltd., China), and the surface

111

area-to-weight ratio was calculated by surface area/ weight.32-33 A three-dimensional laser

112

scanner was used for this study. The surface area-to-weight ratio was used to express the

113

result in Table 1.

114

Preparation of LTCRU. To make bio-based coated fertilizers, 3 kg of LTUs were put in a

115

rotating drum in a coating machine (Taizhou Liming pharmaceutical machinery Co., LTD,

5 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

116

China) and preheated by blasting hot air of 70±2 °C. Then 30g of the mixture of coating

117

materials (15 g of bio-polyol and 15 g of MDI) were sprayed onto the surfaces of LTUs. The

118

heat-curing reaction of the mixed coating materials was finished in the rotating drum in 15

119

min and the coating materials were coated on the surfaces of the fertilizers by forming a layer

120

of coating. This process was repeated for six times to make LTCRU1, eight times to make

121

LTCRU2. The actual percentage of coating material in each coated fertilizer was determined

122

by measuring coating materials used as following. The 50 g of a coated fertilizer was crushed

123

and placed into 80 ml deionized water to dissolve urea out of the coating. The remaining

124

material was dried at 60±5 °C for 4 h. The weight of coating materials used was recoded. The

125

percentage of both coating material and N contents in the LTCRUs are listed in Table 2. The

126

actual coating content ranged from 1.83-3.04%. The use efficiency of coating materials is not

127

high with a rotating drum used in this study and could be much high with a fluidized bed

128

coating equipment commonly used for the scale-up production.

129

To make the modified bio-based coated fertilizers, 2.5 g of the NFS particles (0.5 wt. % of

130

the coating) were first dispersed in both 500.0 g of bio-polyol and 500.0 g of MDI through

131

fast stirring and ultra-sonication for an hour.34-38 Then, 15.0 g of each dispersion was mixed

132

and dropped onto the surfaces of the fertilizer particles in the rotation drum. The same coating

133

procedures were applied to prepare the modified fertilizers, which were labeled

134

correspondingly as MLTCRU1 and MLTCRU2.

135

Characterization of LTCRU and MLTCRU Coatings. The coatings of LTCRU and

136

MLTCRU were dried at 65 °C for 24 h. They were then analyzed by a Fourier Transform

137

Infrared (FTIR) spectroscopy (Nicolet IS10) at the wavenumber range of 4000 to 500 cm-1.

138

With the help of the scanning electron microscopy coupled with energy dispersive X-ray

139

Spectroscopy (SEM-EDS, FEI Quanta 650 and SU8010), the morphologies and element

140

compositions of the coatings were determined under high-vacuum conditions. Metal spraying

6 ACS Paragon Plus Environment

Page 6 of 30

Page 7 of 30

Journal of Agricultural and Food Chemistry

141

was used to increase the electro-conductivity of these samples for better SEM images. The

142

water contact angle (WCA) of the coating materials of LTCRU and MLTCRU were measured

143

with an optical contact angle meter (Powereach, JC2000C2).

144

Nitrogen Release Characteristics of LTCRU and MLTCRU. The percentages of N

145

content released from LTCRU and MLTCRU in the first 24 h were measured in still deionized

146

water at 25 °C. Five tablets (10.00±0.75g, three replicates) were placed in a glass bottle

147

containing 200 mL of deionized water and kept in an incubator at 25±0.5 °C. The amount of

148

N released from the coated fertilizers at 1, 3, 5, 7, 10, 14, 28, 56, 84, 112 and 140 days were

149

measured with the Kjeldahl method.19 When the cumulative N release reached or was over 80 %

150

of the total N, the coated fertilizers were taken out from the bottles. The release characteristics

151

of single LTCRU or MLTCRU in deionized water were also determined in a 50 mL centrifuge

152

tube at 25 °C. Incubation conditions and experimental method were the same. The amount of

153

N released from the coated fertilizers at 1, 3, 5, 7, 10, 14, 28, 56, 84 days were measured with

154

the Kjeldahl method.

155

RESULTS AND DISCUSSION

156

Comparison of Urea Prill and LTU. Three-dimensional scanning technology was used to

157

measure the volumes and surface areas of the fertilizers in graphic models (Figure 1a1, b1).

158

After being mechanically molded, urea prills (Figure 1a1, 2.00-4.00 mm average diameter and

159

0.03±0.01 g average weight) became LTU (Figure 1b1, 16.00 mm of diameter and 2.00±0.15 g

160

average weight). After the mechanical extruding, the shape of LTU was more regular than that

161

of urea prill. The surface area of the fertilizers was measured (Table 1). The surface

162

area-to-weight ratio of LTU was 359.36 mm2·g-1 which is much less than that of urea prill

163

(1257.78 mm2·g-1). The SEM analysis with two magnifications was performed to compare the

164

surface morphology of the urea prill and LTU. For the images of 30× magnifications, the

165

surfaces of urea prill and LTU showed no clear differences (Figure 1a2, b2). At 200×

7 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

166

magnification, the surface of urea prill showed small bumps (Figure 1a3). As a result, LTU is a

167

better core than the urea prill for the production of coated fertilizer because of its smoother

168

surface and lower surface area-to-weight ratio.39-40 The coating of LTU may also use less

169

materials and thus has lower production cost than that of urea prill.13

170

Photographs of Coating Materials and Fertilizers. Bio-polyol, bio-polyol mixed with

171

NFS particles, MDI and MDI mixed with NFS particles were respectively put into four glass

172

bottles and then stewed for two months in an incubator at 25±0.5 °C to verify the stability of

173

NFS in coating materials. NFS remained uniformly dispersed in the bio-based polyols,

174

demonstrating great stability without coagulation or other types of inter-facial instability

175

(Figure 2Ab). However, NFS caused solidification in MDI (Figure 2Ad) due to the reaction

176

between Si-O of NFS and NCO groups of MDI. These results suggest that fumed silica should

177

be dispersed in bio-based polyols to avoid potential aggregations when used to prepare

178

coating materials for controlled-release fertilizers. The coating materials in Figure 2A were

179

uniformly coated onto the surfaces of LTU in the rotating drum to make the LTCRU1 and

180

MLTCRU1 (Figure 2C). The entire LTUs including edges were coated with the bio-based

181

material. With the addition of NFS, the coating of MLTCRU showed a smoother surface than

182

that of LTCRU, which can improve mechanical properties.41-44

183

FTIR Spectra of LTCRU and MLTCRU Coatings. The coating structures of MLTCRU,

184

LTCRU, MDI and bio-based polyol were examined by FTIR (Figure 3). The NH-CO at 1601

185

cm-1 in Figure 3c and Figure 3d suggests the existence of polyurethane after the reaction

186

between bio-based polyol (Figure 3a) and MDI (Figure 3b).45 The Si-O stretching of the

187

fumed silica located at 1100 cm-1 overlapped with the 1080 cm-1 absorption band of the

188

C-O-C stretching. Compared with LTCRU, MLCRU showed a larger peak at this wavelength

189

from the absorption of NFS. It is also noteworthy that the spectra of MLTCRU and LTCRU

190

show high intensity of NCO at 2280 cm-1, suggesting that the coating might contain unreacted

8 ACS Paragon Plus Environment

Page 8 of 30

Page 9 of 30

Journal of Agricultural and Food Chemistry

191

isocyanate. In addition, the lowered relative ratios of peaks at 2280 cm-1 of MLTCRU can be

192

attributed to the reaction between NFS and MDI via cross-linking of OH groups as the same

193

phenomenon in Figure 2A.36, 38

194

Morphology of Coatings. The morphologies of the fertilizer coating surfaces and their

195

water contact angles are demonstrated in Figure 4. The surface morphology of LTCRU1

196

(Figure 4a1) presented a wrinkled and porous appearance with a water contact angle of

197

30.57±1.08°. After being modified by the NFS, the water contact angle increased by about 5°

198

to 35.11±0.46°. No clearly changes of hydrophobic property of coating surfaces were found

199

after the modification because NFS was dispersed uniformly in the coatings including surface

200

and cross section. The cross-section morphologies of the LTCRU1 and MLTCRU1 coatings

201

are demonstrated in Figure 4a3 and 4b3, respectively. Pores with diameters even larger than 20

202

µm were found in the coating of LTCRU1 (Figure 4a3). However, large pores were not

203

detected in the coating of MLTCRU1 (Figure 4b3) indicating that the addition of NFS can

204

reduce the porosity of the coatings. The images showed presence and distribution of the NFS

205

in MLTCRU1 coatings (Figure 4b2 and 4b4) but not in LTCRU1 coating (Figure 4a2 and 4a4).

206

NFS particles were found in the surface and cross section of MLTCRU1 coatings (Figure 4b2

207

and 4b4). The differences between LTCRU1, MLTCRU1 and LTCRU2, MLTCRU2 are only

208

coating contents. Therefore, the morphology of LTCRU2 and MLTCRU2 were put in Figure

209

S1 in Supporting Information.

210

Nitrogen Release Characteristics of LTCRU and MLTCRU. The most important

211

characteristic of coated fertilizers is their slow-release property.18 The N release characteristic

212

curves of LTCRU1, LTCRU2, MLTCRU1 and MLTCRU2 are presented in Figure 5 and four

213

mathematical models were derived based N release data. The N release rates can be calculated

214

based on the following four equations:

215

For LTCRU1: y = 11.98ln(x) + 39.44, R2 = 0.8340;

9 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

216

For LTCRU2: y = 0.67x + 1.99, R2 = 0.9967;

217

For MLTCRU1: y = 10.51ln(x) + 31.88, R2 = 0.8487;

218

For MLTCRU2: y = 0.60x - 1.82, R2 = 0.9727.

219

Where Y is the nitrogen accumulative release (%) and X is the incubation time (days). The

220

N initial release rates during the first seven days for LTCRU1 and MLTCRU1 (both had 2 wt. %

221

coating) were almost identical without notable differences. When the incubation time reached

222

28 days, LTCRU1 had reached a cumulative N release rate of 89.38±4.13 %, but the

223

corresponding release rate of MLTCRU1 was only 74.40±3.75 %. The International standard

224

for CRFs (ISO 18644-2016) is that cumulative release mass fraction of nutrient in 28 days

225

should be less than 75%.46 Therefore, MLTCRU1 reduced the release rate by 15 % compared

226

to LTCRU1 and met the standard.

227

When the coating increased to 3 wt. % and the incubation time reached seventh day, the

228

cumulative N release rates of LTCRU2 and MLTCRU2 were 7.14±3.12 % and 5.44±3.15 %,

229

respectively which were not significantly different. After 28 days, the cumulative N release

230

rate of LTCRU2 reached 23.87±1.32 %, almost twice of the corresponding release rate of

231

MLTCRU2 (12.02±1.99 %). Even though both LTCRU2 and MLTCRU2 met the ISO

232

standard, MLTCRU2 showed the superior release behavior to fit crops which are slow growth

233

and low nutrient demand during first 28 days.

234

N release characteristics of the coated fertilizers are significantly affected by the contents

235

of the coating materials. In this study, when the coating contents increased from 2 wt. % to 3

236

wt. %, the N release longevity of the coated fertilizers increased significantly. When the

237

coating content was 2 wt. %, N release of LTCRU1 and MLTCRU1 were 92.98±1.24 % and

238

90.05±1.86 % after 84 days incubation. When the coating content was added to 3 wt. %, N

239

release of LTCRU2 and MLTCRU2 were 58.42±2.10 % and 40.25±1.68 % after 84 days

240

incubation. The N release longevity of LTCRU2 and MLTCRU2 were prolonged to about 140

10 ACS Paragon Plus Environment

Page 10 of 30

Page 11 of 30

Journal of Agricultural and Food Chemistry

241

days when the N accumulative release was 93.84±1.15 % and 90.24±1.83 %, respectively. As

242

the coating materials increase on the fertilizer layer by layer, the liquid pathways of water and

243

dissolved urea had to diffuse through more layers to get in and out which solw the release of

244

fertilizers. Therefore, with more coating contents, LTCRU2 and MLTCRU2 have a bettter

245

controlled-release capacity than LTCRU1 and MLTCRU1, respectively. In addition, the

246

results indicate that NFS modification can significantly improve the N release longevity of

247

coated fertilizers. Previous studies have shown that NFS can modify PU resulting in improved

248

rheological properties, hydrophobic surface, mechanical properties, and thermal stability with

249

small amount of addition.34 As a result, the controlled-release property of modified coating is

250

enhanced.47

251

Releasing Patterns of CRU. The N release from the CRUs may have two different release

252

patterns. For the first patter (LTCRU), the release can be divided into four stages (Figure 6).

253

After being dropped into deionized water, LTCRU fertilizers with pores on their coatings

254

started absorbing water to show the first release stage, the wetting stage. Water absorption and

255

wetting of the coating material led to the initial releasing stage (Figure 6a). During this stage,

256

water passed through the pores on the coating and dissolved the urea out of the coating from

257

one side which bigger holes existed, thereby causing the release of N with more urea loss, the

258

urea core of LTCRU became irregular and incomplete and there existed an obvious

259

permeation pressure difference between the inside and outside of the coating, leading to the

260

fast dissolution (Figure 6b) and slow dissolution (Figure 6c) stages. The shape and position of

261

the urea core remaining in the coating depended on the locations of the release pores. Finally,

262

the entire urea core in the coating was dissolved; the nutrient concentration within the coating

263

began to decrease during the release, slowing down overall fertilizer release rate. The final

264

permeation stage (Figure 6d) showed a slower steady release characteristic in comparison to

265

other stages because N concentration inside the coating and the permeation pressure

11 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

266

decreased.

267

MLTCRU fertilizers followed the release pattern 2 (Figure 7). During the wetting stage in

268

the first three days, there was no change in N release and fertilizer volume (Figure 7a). In the

269

dissolution stage, water or vapor went through the coating and slowing N release without

270

notable fertilizer volume changes (Figure 7b). At the end of this stage, a thin layer of water

271

between the urea core and coating was visually observed. With more and more urea dissolved

272

in the water inside the coating, the permeation pressure between the inside and outside of the

273

coating increased. As a result, the coating was stretched to decrease the permeation pressure,

274

leading to the increase in fertilizer volume during the swelling stage (Figure 7c). In this stage,

275

there existed both urea core and solution inside the coated fertilizer tablet. As the MLTCRU

276

fertilizer approached its maximum volume, the release rate speeded up. Urea core and

277

solution left inside the coating spread out steadily during the final stage (Figure 7d).

278

A combination of these two release patterns led to a relatively steady characteristic of N

279

release from the LTCRU. Findings from this study indicate that NFS modification can extend

280

the N release longevity of the coated fertilizer. The bio-based LTCRUs demonstrate good

281

controlled-release characteristics and thus can be a promising controlled-release fertilizer for

282

field applications.

12 ACS Paragon Plus Environment

Page 12 of 30

Page 13 of 30

Journal of Agricultural and Food Chemistry

283

ASSOCIATED CONTENT

284

Supporting Information

285

Morphology of coatings (LTCRU2 and MLTCRU2)

286 287

AUTHOR INFORMATION

288

Corresponding Author

289

Tell: +86-538-824-2900 (China)

290

Fax: +86-538-824-2250 (China)

291

Email: [email protected]

292

Acknowledgements

293

This research was funded by the National Natural Science Foundation of China (Grant

294

31572201), National Key R&D Program of China (2017YFD0200702), Shandong Province

295

Key R&D Program (2017CXGC0306), Taishan industrial experts programme

296

(LJNY201609), Shandong Agricultural Innovation Team (Grant SDAIT-17-04), the Project

297

of Shandong Province Education Department (Grant ZR2014JL023 and J16LF01) and

298

Shandong Youth Education Science Program for College Students (Grant 17BSH113).

299

Notes

300

The authors declare no competing financial interest.

13 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

301

REFERENCES

302 303

(1) Azeem, B.; KuShaari, K.; Man, Z. B.; Basit, A.; Thanh, T. H. Review on materials &

304

methods to produce controlled release coated urea fertilizer. J. Controlled Release 2014, 181,

305

11-21.

306

(2) Shaviv, A. In Controlled release fertilizers, IFA international workshop on

307

enhanced-efficiency fertilizers, Frankfurt. International Fertilizer Industry Association Paris,

308

France: 2005; pp 28-30.

309

(3) Geng, J.; Ma, Q.; Chen, J.; Zhang, M.; Li, C.; Yang, Y.; Yang, X.; Zhang, W.; Liu, Z.

310

Effects of polymer coated urea and sulfur fertilization on yield, nitrogen use efficiency and

311

leaf senescence of cotton. Field Crops Res. 2016, 187, 87-95.

312

(4) Geng, J.; Ma, Q.; Zhang, M.; Li, C.; Liu, Z.; Lyu, X.; Zheng, W. Synchronized

313

relationships between nitrogen release of controlled release nitrogen fertilizers and nitrogen

314

requirements of cotton. Field Crops Res. 2015, 184, 9-16.

315

(5) Yang, X.; Geng, J.; Li, C.; Zhang, M.; Chen, B.; Tian, X.; Zheng, W.; Liu, Z.; Wang, C.

316

Combined application of polymer coated potassium chloride and urea improved fertilizer use

317

efficiencies, yield and leaf photosynthesis of cotton on saline soil. Field Crops Res. 2016, 197,

318

63-73.

319

(6) Zheng, W.; Sui, C.; Liu, Z.; Geng, J.; Tian, X.; Yang, X.; Li, C.; Zhang, M. Long-term

320

effects of controlled-release urea on crop yields and soil fertility under wheat–corn double

321

cropping systems. Agron. J. 2016, 108 (4), 1703-1716.

322 323 324 325

(7) Doran, J. W. Soil health and global sustainability: translating science into practice. Agric., Ecosyst. Environ. 2002, 88 (2), 119-127. (8) Lyu, X.; Yang, Y.; Li, Y.; Fan, X.; Wan, Y.; Geng, Y.; Zhang, M. Polymer-coated tablet urea improved rice yield and nitrogen use efficiency. Agron. J. 2015, 107 (5), 1837-1844.

14 ACS Paragon Plus Environment

Page 14 of 30

Page 15 of 30

Journal of Agricultural and Food Chemistry

326

(9) Katyal, J.; Vlek, P. Effect of granule size and the placement geometry on the efficiency of

327

urea supergranules for wetland rice grown on a permeable soil. Fertilizer research 1988, 15

328

(2), 193-201.

329

(10)

Bandaogo, A.; Bidjokazo, F.; Youl, S.; Safo, E.; Abaidoo, R.; Andrews, O. Effect of

330

fertilizer deep placement with urea supergranule on nitrogen use efficiency of irrigated rice in

331

Sourou Valley (Burkina Faso). Nutrient cycling in agroecosystems 2015, 102 (1), 79-89.

332 333 334 335 336

(11)

Sudhakara, K.; Prasad, R. Ammonia volatilization losses from prilled urea, urea

supergranules (USG) and coated USG in rice fields. Plant Soil 1986, 94 (2), 293-295. (12)

Sikder, R.; Xiaoying, J. Urea super granule (USG) as key conductor in agricultural

productivity development in Bangladesh. Developing Country Studies 2014, 4, 132-9. (13)

Yang, Y.-c.; Zhang, M.; Li, Y.; Fan, X.-h.; Geng, Y.-q. Improving the quality of

337

polymer-coated urea with recycled plastic, proper additives, and large tablets. J. Agric. Food

338

Chem. 2012, 60 (45), 11229-11237.

339 340 341 342

(14)

Naz, M. Y.; Sulaiman, S. A. Slow release coating remedy for nitrogen loss from

conventional urea: a review. J. Controlled Release 2016, 225, 109-120. (15)

Martin, E. Trenkel. Improving Fertilizer Use Efficiency Controlled-Release and

Stabilized Fertilizer In Agriculture. International Fertilizer Industry Association 1997.

343

(16)

Randall, D.; Lee, S. The polyurethanes book. Wiley: 2002.

344

(17)

Qiao, D.; Liu, H.; Yu, L.; Bao, X.; Simon, G. P.; Petinakis, E.; Chen, L. Preparation

345

and characterization of slow-release fertilizer encapsulated by starch-based superabsorbent

346

polymer. Carbohydr. Polym. 2016, 147, 146-154.

347

(18)

Xie, L.; Liu, M.; Ni, B.; Wang, Y. Utilization of wheat straw for the preparation of

348

coated controlled-release fertilizer with the function of water retention. J. Agric. Food Chem.

349

2012, 60 (28), 6921-6928.

350

(19)

Zhang, S.; Yang, Y.; Gao, B.; Wan, Y.; Li, Y. C.; Zhao, C. Bio-based interpenetrating

15 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

351

network polymer composites from locust sawdust as coating material for environmentally

352

friendly controlled-release urea fertilizers. J. Agric. Food Chem. 2016, 64 (28), 5692-5700.

353

(20)

Liu, X.; Yang, Y.; Gao, B.; Li, Y. Organic silicone‐modified transgenic soybean oil

354

as bio‐based coating material for controlled‐release urea fertilizers. J. Appl. Polym. Sci.

355

2016, 133 (41).

356

(21)

Xie, J.; Yang, Y.; Gao, B.; Wan, Y.; Li, Y. C.; Xu, J.; Zhao, Q. Biomimetic

357

Superhydrophobic Biobased Polyurethane-Coated Fertilizer with Atmosphere “Outerwear”.

358

ACS applied materials & interfaces 2017, 9 (18), 15868-15879.

359

(22)

Yang, Y.; Tong, Z.; Geng, Y.; Li, Y.; Zhang, M. Biobased polymer composites derived

360

from corn stover and feather meals as double-coating materials for controlled-release and

361

water-retention urea fertilizers. J. Agric. Food Chem. 2013, 61 (34), 8166-8174.

362

(23)

Picca, R. A.; Paladini, F.; Sportelli, M. C.; Pollini, M.; Giannossa, L. C.; Di Franco,

363

C.; Panico, A.; Mangone, A.; Valentini, A.; Cioffi, N. Combined approach for the

364

development of efficient and safe nanoantimicrobials: The case of nanosilver-modified

365

polyurethane foams. ACS Biomaterials Science & Engineering 2016, 3 (7), 1417-1425.

366

(24)

Lü, X.; Cui, Z.; Wei, W.; Xie, J.; Jiang, L.; Huang, J.; Liu, J. Constructing

367

polyurethane sponge modified with silica/graphene oxide nanohybrids as a ternary sorbent.

368

Chem. Eng. J. 2016, 284, 478-486.

369

(25)

Zhang, S.; Yang, Y.; Gao, B.; Li, Y. C.; Liu, Z. Superhydrophobic controlled-release

370

fertilizers coated with bio-based polymers with organosilicon and nano-silica modifications.

371

Journal of Materials Chemistry A 2017, 5 (37), 19943-19953.

372 373 374 375

(26)

Shavit, U.; Reiss, M.; Shaviv, A. Wetting mechanisms of gel-based controlled-release

fertilizers. J. Controlled Release 2003, 88 (1), 71-83. (27)

Shavit, U.; Shaviv, A.; Shalit, G.; Zaslavsky, D. Release characteristics of a new

controlled release fertilizer. J. Controlled Release 1997, 43 (2-3), 131-138.

16 ACS Paragon Plus Environment

Page 16 of 30

Page 17 of 30

376 377 378

Journal of Agricultural and Food Chemistry

(28)

Mutlu, H.; Meier, M. A. Castor oil as a renewable resource for the chemical industry.

Eur. J. Lipid Sci. Technol. 2010, 112 (1), 10-30. (29)

Jeon, H.; Kim, M.-N.; Park, E.-S. Thermal, mechanical and biodegradation properties

379

of pure, epoxidized and methoxylated castor oil based polyurethane. Plastics, Rubber and

380

Composites 2016, 45 (1), 1-8.

381

(30)

Oprea, S.; Potolinca, V. O.; Gradinariu, P.; Joga, A.; Oprea, V. Synthesis, properties,

382

and fungal degradation of castor-oil-based polyurethane composites with different cellulose

383

contents. Cellu 2016, 23 (4), 2515-2526.

384

(31)

Das, S.; Pandey, P.; Mohanty, S.; Nayak, S. K. Evaluation of biodegradability of

385

green polyurethane/nanosilica composite synthesized from transesterified castor oil and palm

386

oil based isocyanate. Int. Biodeterior. Biodegrad. 2017, 117, 278-288.

387

(32)

Igathinathane, C.; Davis, J. D.; Purswell, J. L.; Columbus, E. P. Application of 3D

388

scanned imaging methodology for volume, surface area, and envelope density evaluation of

389

densified biomass. Bioresour. Technol. 2010, 101 (11), 4220-4227.

390

(33)

Sholts, S. B.; Wärmländer, S. K. T. S.; Flores, L. M.; Miller, K. W. P.; Walker, P. L.

391

Variation in the Measurement of Cranial Volume and Surface Area Using 3D Laser Scanning

392

Technology. J. Forensic Sci. 2010, 55 (4), 871-876.

393

(34)

Verdolotti, L.; Lavorgna, M.; Lamanna, R.; Di Maio, E.; Iannace, S.

394

Polyurethane-silica hybrid foam by sol–gel approach: Chemical and functional properties.

395

Polymer 2015, 56, 20-28.

396

(35)

Hassanajili, S.; Masoudi, E.; Karimi, G.; Khademi, M. Mixed matrix membranes

397

based on polyetherurethane and polyesterurethane containing silica nanoparticles for

398

separation of CO2/CH4 gases. Sep. Purif. Technol. 2013, 116, 1-12.

399 400

(36)

Pingan, H.; Mengjun, J.; Yanyan, Z.; Ling, H. A silica/PVA adhesive hybrid material

with high transparency, thermostability and mechanical strength. RSC Advances 2017, 7 (5),

17 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

401 402

2450-2459. (37)

Serkis, M.; Poręba, R.; Hodan, J.; Kredatusová, J.; Špírková, M. Preparation and

403

characterization of thermoplastic water ‐ borne polycarbonate ‐ based polyurethane

404

dispersions and cast films. J. Appl. Polym. Sci. 2015, 132 (42).

405 406 407

(38)

Wu, S.-H.; Mou, C.-Y.; Lin, H.-P. Synthesis of mesoporous silica nanoparticles.

ChSRv 2013, 42 (9), 3862-3875. (39)

Ho, L.; Cuppok, Y.; Muschert, S.; Gordon, K. C.; Pepper, M.; Shen, Y.; Siepmann, F.;

408

Siepmann, J.; Taday, P. F.; Rades, T. Effects of film coating thickness and drug layer

409

uniformity on in vitro drug release from sustained-release coated pellets: A case study using

410

terahertz pulsed imaging. Int. J. Pharm. 2009, 382 (1), 151-159.

411

(40)

Strawhecker, K. E.; Kumar, S. K.; Douglas, J. F.; Karim, A. The Critical Role of

412

Solvent Evaporation on the Roughness of Spin-Cast Polymer Films. Macromolecules 2001,

413

34 (14), 4669-4672.

414

(41)

Han, Y.; Chen, Z.; Dong, W.; Xin, Z. Improved water resistance, thermal stability,

415

and mechanical properties of waterborne polyurethane nanohybrids reinforced by fumed silica

416

via in situ polymerization. HPP 2015, 27 (7), 824-832.

417

(42)

Hassanajili, S.; Sajedi, M. T. Fumed silica/polyurethane nanocomposites: effect of

418

silica concentration and its surface modification on rheology and mechanical properties.

419

Iranian Polymer Journal 2016, 25 (8), 697-710.

420

(43)

Sankar, S.; Sanjeev, S.; Sharma, D. Synthesis and characterization of mesoporous

421

SiO2 nanoparticles synthesized from Biogenic Rice Husk Ash for optoelectronic applications.

422

An International Journal of Engineering Sciences 2016, 17, 353-358.

423

(44)

Wang, X.; Dou, L.; Li, Z.; Yang, L.; Yu, J.; Ding, B. Flexible hierarchical ZrO2

424

nanoparticle-embedded SiO2 nanofibrous membrane as a versatile tool for efficient removal

425

of phosphate. ACS applied materials & interfaces 2016, 8 (50), 34668-34676.

18 ACS Paragon Plus Environment

Page 18 of 30

Page 19 of 30

426

Journal of Agricultural and Food Chemistry

(45)

Yang, Y.; Wei, Z.; Wang, C.; Tong, Z. Versatile fabrication of nanocomposite

427

microcapsules with controlled shell thickness and low permeability. ACS applied materials &

428

interfaces 2013, 5 (7), 2495-2502.

429

(46)

ISO Fertilizers and soil conditioners —Controlled-release fertilizer —General

430

requirements. The International Organization for Standardization: Switzerland, 2016; Vol.

431

ISO 18644:2016(E).

432

(47)

Cai, D.; Wang, L.; Zhang, G.; Zhang, X.; Wu, Z. Controlling pesticide loss by natural

433

porous micro/nano composites: straw ash-based biochar and biosilica. ACS applied materials

434

& interfaces 2013, 5 (18), 9212-9216.

435

19 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 20 of 30

436

Table captions

437

Table 1. Physical properties of urea prills and Large Tablets Urea (LTUs).

438

Table 2. Composition of various coated fertilizers.

439 440

Figure captions

441

Figure 1. Three-dimensional scanning images of urea prill (a1) and Large Tablet Urea (LTU)

442

(b1) and scanning electron microscopy (SEM) images of urea prill (a2, 30×; a3, 200×) and

443

LTU (b2, 30×; b3, 200×).

444

Figure 2. (A) Photograph of coating materials: bio-polyol (a), bio-polyol mixed with Nano

445

Fumed Silica (NFS) particles (b), Methylene diphenyl diisocyanate (MDI) (c) and MDI mixed

446

with NFS particles (d). (B) Schematic diagram of the synthesis of Large Tablet

447

Controlled-Release Urea (LTCRU) and Modified Large Tablet Controlled-Release Urea

448

(MLTCRU). (C) Photograph of conventional urea pills (U), Large Tablet Urea (LTU), Large

449

Tablet Controlled-Release Urea (LTCRU) and Modified Large Tablet Controlled-Release

450

Urea (MLTCRU).

451

Figure 3. Fourier Transform Infrared (FTIR) spectra of bio-based polyol (a), Methylene

452

diphenyl diisocyanate (MDI) (b), coatings of Large Tablet Controlled-Release Urea (LTCRU)

453

(c) and Modified Large Tablet Controlled-Release Urea (MLTCRU) (d).

454

Figure 4. Scanning electron microscopy coupled with energy dispersive X-ray Spectroscopy

455

(SEM-EDS) images and corresponding water contact angles of surfaces of Large Tablet

456

Controlled-Release

457

Controlled-Release Urea 1 (MLTCRU1) (b1, 200×), and cross sections of LTCRU1 (a3,

458

2,000×) and MLTCRU1 (b3, 2,000×). EDS spectra of LTCRU1 surface (a2), EDS spectra of

459

MLTCRU1 surface (b2), EDS spectra of cross section of LTCRU1 (a4) and EDS spectra of

460

cross section of MLTCRU1 (b4).

Urea

1

(LTCRU1)

(a1,

200×)

20 ACS Paragon Plus Environment

and

Modified

Large

Tablet

Page 21 of 30

Journal of Agricultural and Food Chemistry

461

Figure 5. Nitrogen release characteristics of Large Tablet Controlled-Release Urea 1

462

(LTCRU1) (a), LTCRU2 (b), Modified Large Tablet Controlled-Release Urea 1 (MLTCRU1)

463

(c) and MLTCRU2 (d) at 25 °C in deionized water. (a, y = 11.98ln(x) + 39.44, with R2 =

464

0.8340; b, y = 0.67x + 1.99, with R2 = 0.9967; c, y = 10.51ln(x) + 31.88, with R2 = 0.8487; d,

465

y = 0.60x - 1.82, with R2 = 0.9727).

466

Figure 6. Relationship between nitrogen (N) release rates (%) and volume change (%) of

467

Large Tablet Controlled-Release Urea (LTCRU) at four stages (a, b, c, and d) of the pattern

468

one. The top photo showed the actual sizes of LTCRU at these stages: initial dissolution stage

469

(a, 0-3rd day, no volume change), fast dissolution stage (b, 3-10th day, no volume change),

470

slow dissolution stage (c, 10-28th day, no volume change) and final stage (d, after 28th day,

471

no volume change). The figure on the bottom showed measured fertilizer volumes: a, 100%, b,

472

100%, c, 100%, and d, 100%. at four stages.

473

Figure 7. Relationship between nitrogen (N) release rates (%) and volume change (%) of

474

Modified Large Tablet Controlled-Release Urea (MLTCRU) at four stages (a, b, c, and d) of

475

the pattern two. The top photo showed the actual sizes of MLTCRU at these stages: wetting

476

stage (a, 0-3rd day, no volume change), dissolution stage (b, 3-14th day, larger), swelling

477

stage (c, 14-28th day, largest) and final stage (d, after 27th day, decreased). The figure on the

478

bottom showed measured fertilizer volumes: a, 100%, b, 100-106%, c, 106-111%, and d,

479

111-106%. at four stages.

21 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

480

Page 22 of 30

Table 1. Physical properties of urea prills and Large Tablets Urea (LTUs). Mass (g)

Volume (mm3)

Surface area (mm2)

Surface area-to-weight ratio (mm2 g-1)

Urea prills

0.03±0.01

26.35±5.09

43.65±7.88

1257.78

LTUs

2.00±0.15

1726.25±32.45

733.63±50.39

359.36

481 482

Table 2. Composition of various coated fertilizers. Fertilizers LTCRU1 LTCRU2

β

β

MLTCRU1 MLTCRU2

γ

γ

Design of coating content

Actual coating content

Total N α

(wt. %)

(wt. %)

(wt. %)

2

2.05±0.06

45.25±0.06

3

3.04±0.15

44.80±0.15

2

1.83±0.11

45.35±0.11

3

2.87±0.12

44.87±0.12

α

the total Nitrogen (N) content was calculated based on the actual coating content.

β

LTCRU: Large Tablet Controlled-Release Urea.

γ

MLTCRU: Modified Large Tablet Controlled-Release Urea.

483

22 ACS Paragon Plus Environment

Page 23 of 30

Journal of Agricultural and Food Chemistry

484 485

Figure 1. Three-dimensional scanning images of urea prill (a1) and Large Tablet Urea (LTU)

486

(b1) and scanning electron microscopy (SEM) images of urea prill (a2, 30×; a3, 200×) and

487

LTU (b2, 30×; b3, 200×).

23 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

488 489

Figure 2. (A) Photograph of coating materials: bio-polyol (a), bio-polyol mixed with Nano

490

Fumed Silica (NFS) particles (b), Methylene diphenyl diisocyanate (MDI) (c) and MDI

491

mixed with NFS particles (d). (B) Schematic diagram of the synthesis of Large Tablet

492

Controlled-Release Urea (LTCRU) and Modified Large Tablet Controlled-Release Urea

493

(MLTCRU). (C) Photograph of conventional urea pills (U), Large Tablet Urea (LTU), Large

494

Tablet Controlled-Release Urea (LTCRU) and Modified Large Tablet Controlled-Release

495

Urea (MLTCRU).

24 ACS Paragon Plus Environment

Page 24 of 30

Page 25 of 30

Journal of Agricultural and Food Chemistry

496 497

Figure 3. Fourier Transform Infrared (FTIR) spectra of bio-based polyol (a), Methylene

498

diphenyl diisocyanate (MDI) (b), coatings of Large Tablet Controlled-Release Urea (LTCRU)

499

(c) and Modified Large Tablet Controlled-Release Urea (MLTCRU) (d).

25 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

Page 26 of 30

500 501

Figure 4. Scanning electron microscopy coupled with energy dispersive X-ray Spectroscopy

502

(SEM-EDS) images and corresponding water contact angles of surfaces of Large Tablet

503

Controlled-Release

504

Controlled-Release Urea 1 (MLTCRU1) (b1, 200×), and cross sections of LTCRU1 (a3,

505

2,000×) and MLTCRU1 (b3, 2,000×). EDS spectra of LTCRU1 surface (a2), EDS spectra of

Urea

1

(LTCRU1)

(a1,

200×)

26 ACS Paragon Plus Environment

and

Modified

Large

Tablet

Page 27 of 30

Journal of Agricultural and Food Chemistry

506

MLTCRU1 surface (b2), EDS spectra of cross section of LTCRU1 (a4) and EDS spectra of

507

cross section of MLTCRU1 (b4).

508

100

a

Nitrogen accumulative release (%)

c

b

80 d

60 a - LTCRU1 b - LTCRU2 c - MLTCRU d - MLTCRU2

40

a: b: c: d:

20

y y y y

= = = =

11.98ln(x) + 39.44 0.67x + 1.99 10.51ln(x) + 31.88 0.60x - 1.82

R2 = 0.8340 R2 = 0.9967 R2 = 0.8487 R2 = 0.9727

0 0

10

20

30

40

50

60

70

80

90

100 110 120 130 140

509

Incubation time (days)

510

Figure 5. Nitrogen release characteristics of Large Tablet Controlled-Release Urea 1

511

(LTCRU1) (a), LTCRU2 (b), Modified Large Tablet Controlled-Release Urea 1 (MLTCRU1)

512

(c) and MLTCRU2 (d) at 25 °C in deionized water. (a, y = 11.98ln(x) + 39.44, with R2 =

513

0.8340; b, y = 0.67x + 1.99, with R2 = 0.9967; c, y = 10.51ln(x) + 31.88, with R2 = 0.8487; d,

514

y = 0.60x - 1.82, with R2 = 0.9727).

27 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

515 516

Figure 6. Relationship between nitrogen (N) release rates (%) and volume change (%) of

517

Large Tablet Controlled-Release Urea (LTCRU) at four stages (a, b, c, and d) of the pattern

518

one. The top photo showed the actual sizes of LTCRU at these stages: initial dissolution stage

519

(a, 0-3rd day, no volume change), fast dissolution stage (b, 3-10th day, no volume change),

520

slow dissolution stage (c, 10-28th day, no volume change) and final stage (d, after 28th day,

521

no volume change). The figure on the bottom showed measured fertilizer volumes: a, 100%, b,

522

100%, c, 100%, and d, 100% at four stages.

28 ACS Paragon Plus Environment

Page 28 of 30

Page 29 of 30

Journal of Agricultural and Food Chemistry

523 524

Figure 7. Relationship between nitrogen (N) release rates (%) and volume change (%) of

525

Modified Large Tablet Controlled-Release Urea (MLTCRU) at four stages (a, b, c, and d) of

526

the pattern two. The top photo showed the actual sizes of MLTCRU at these stages: wetting

527

stage (a, 0-3rd day, no volume change), dissolution stage (b, 3-14th day, larger), swelling

528

stage (c, 14-28th day, largest) and final stage (d, after 27th day, decreased). The figure on the

529

bottom showed measured fertilizer volumes: a, 100%, b, 100-106%, c, 106-111%, and d,

530

111-106% at four stages.

29 ACS Paragon Plus Environment

Journal of Agricultural and Food Chemistry

For Table of contents use only Bio-based Large Tablet Controlled-Release Urea: Synthesis, Characterization, and Controlled-Released Mechanisms

TOC (ART) 531

Modified bio-based material improved the slow-release properties of LTCRU by reducing

532

surface area-to-weight ratio and generating two nitrogen release patterns.

30 ACS Paragon Plus Environment

Page 30 of 30