Characterization of a Thermoresponsive Chitosan Derivative as a

Sep 30, 2016 - Department of Chemical Engineering, University of Arkansas, Fayetteville, ... For a more comprehensive list of citations to this articl...
0 downloads 0 Views 1MB Size
Subscriber access provided by La Trobe University Library

Article

Characterization of a Thermoresponsive Chitosan Derivative as a Potential Draw Solute for Forward Osmosis Rumwald Leo G. Lecaros, Zih-Chi Syu, Yu-Hsuan Chiao, S. Ranil Wickramasinghe, Yan Li Ji, Quanfu An, Wei-Song Hung, Chien-Chieh Hu, Kueir-Rarn Lee, and Juin-Yih Lai Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.6b02102 • Publication Date (Web): 30 Sep 2016 Downloaded from http://pubs.acs.org on October 2, 2016

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 free 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 accessible to all readers and 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.

Environmental Science & Technology 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 24

Environmental Science & Technology

1

Characterization of a Thermoresponsive Chitosan

2

Derivative as a Potential Draw Solute for Forward

3

Osmosis

4

Rumwald Leo G. Lecarosa, Zih-Chi Syua, Yu-Hsuan Chiaob, S Ranil Wickramasingheb, Yan-Li

5

Jia, c, Quan-Fu Anc, Wei-Song Hunga*, Chien-Chieh Hua, Kueir-Rarn Leea, and Juin-Yih Laia

6

a

7

Yuan University, Chung Li 32023, Taiwan

8

b

9

United States

R&D Center for Membrane Technology and Department of Chemical Engineering, Chung

Department of Chemical Engineering, University of Arkansas, Fayetteville, Arkansas 72701,

10

c

11

Polymer Science & Engineering, Zhejiang University, Hangzhou 310027, China

MOE Key Laboratory of Macromolecular Synthesis and Functionalization, Department of

12 13 14 15 16

KEYWORDS: Thermoresponsive polymer, Draw solute, Forward osmosis

17

ACS Paragon Plus Environment

Environmental Science & Technology

18

Abstract

19

A thermoresponsive chitosan derivative was synthesized by reacting chitosan (CS) with butyl

20

glycidyl ether (BGE) to break the inter- and intramolecular hydrogen bonds of the polymer. An

21

aqueous solution of the thermoresponsive CS derivative exhibits a lower critical solution

22

temperature (LCST) than CS, and it undergoes a phase transition separation when the

23

temperature changes. Successful incorporation of BGE into the CS was confirmed by FTIR and

24

XPS analyses. Varying the BGE content and the concentration of the aqueous solution produced

25

different LCST ranges, as shown by transmittance vs. temperature curves. The particle size was

26

observed by scanning electron microscopy, which revealed that the particles were smaller and

27

well dispersed at 15 °C, whereas the particles became larger and tended to aggregate at 60 °C. A

28

similar trend was observed with the mean particle size measured using dynamic light scattering.

29

Positron annihilation lifetime spectroscopy data also revealed the reversibility of the particle

30

properties as a function of temperature. Microstructure analysis showed that the particles had

31

larger free-volume sizes at 15 °C than at 60 °C. The particles were also found to be non-toxic

32

with 92% cell survival. A simple forward osmosis (FO) test for dye dehydration revealed the

33

potential use of the thermoresponsive chitosan derivative as a draw solute with a flux of 8.6

34

L/m2h and rejection of 99.8 %.

35

ACS Paragon Plus Environment

Page 2 of 24

Page 3 of 24

36

Environmental Science & Technology

Introduction

37

Thermoresponsive polymers dissolve in aqueous solution at temperatures below their

38

lower critical solution temperature (LCST) and are phase separated at temperatures above their

39

LCST. Such stimuli-responsive polymers are important and have attracted much attention due to

40

their diverse applications in biomedicine1 and separation processes.2-7 LCST behavior is

41

observed when the inter- and intramolecular interactions vary with increasing temperature.8, 9

42

Thus, grafting hydrophobic groups onto the polymer chain can tune the thermoresponsive

43

behavior by disrupting the inter- and intramolecular hydrogen bonds of the polymers.1

44

Thermoresponsive materials based on natural polymers have drawn great interest because of

45

their attractive properties, which include biocompatibility, biodegradability and non-toxicity.

46

Chitosan (CS), the partially acetylated cationic (1,4)-2-amino-2-deoxy-β-D-glucan, possesses

47

these distinct properties, which makes it a good candidate for various applications. CS is only

48

soluble in dilute aqueous acid solution. It has two reactive groups (amino and hydroxyl groups)

49

where a monomer can be added through different chemical modification techniques, potentially

50

changing or enhancing its properties.10, 11

51

One of the modern day concerns is having a sufficient supply of potable water for the

52

future. The forward osmosis (FO) process has currently gained attention as an alternative method

53

of desalination12

54

less than reverse osmosis.14-18 An ideal FO membrane is capable of providing high water

55

permeability, high rejection of solutes, substantially reducing internal concentration polarization

56

(ICP), and has high chemical stability and mechanical strength. Likewise, a good draw solution

57

must have the following characteristics: high water flux, minimal reverse draw solute flux, no

58

toxicity, reasonably low cost, and easy recovery. Meanwhile, it is required to be compatible with

13

because it does not require high pressures, it is easy to operate, and it costs

ACS Paragon Plus Environment

Environmental Science & Technology

59

the FO membrane. Commonly available compounds as draw solutes can be classified into four

60

types according to their physicochemical properties: volatile compounds, saccharides, inorganic

61

salts, and organic salts and polymers.19-21 Butyl glycidyl ether (BGE) covalently bound to starch

62

molecules has been previously demonstrated to undergo phase separation above its LCST.1 Other

63

research has shown that a thermoresponsive cellulose ether composed of BGE was grafted onto

64

hydroxyethyl cellulose and exhibited both LCST behavior and a critical flocculation temperature

65

(CFT). This thermoresponsive cellulose ether was able to encapsulate dyes at temperatures above

66

its LCST and to separate them from water at temperatures above the CFT.2 In another case, an

67

ionic liquid at temperatures below its upper critical solution temperature (UCST) has been used

68

in FO as a draw solute in treating high-salinity water;4 hydrophilic magnetic nanoparticles have

69

also been used as draw solutes in FO.22, 23

70

Herein, we developed a non-toxic draw solute using CS that has been modified using the

71

hydrophobic monomer BGE, resulting in LCST behavior. The two reactive groups of CS, amine

72

and hydroxyl groups, act as nucleophiles that attack the epoxide ring of BGE. In the case of the

73

hydroxyl group of CS, it must first be attacked by a strong base such as NaOH, followed by the

74

opening of the epoxide ring. The resulting draw solute was subsequently used in forward

75

osmosis with Congo Red dye as the feed solution.

ACS Paragon Plus Environment

Page 4 of 24

Page 5 of 24

76

Environmental Science & Technology

Experimental Section

77 78

Scheme 1. Synthesis of the thermoresponsive chitosan derivative and a schematic of its LCST

79

behavior.

80

Materials

81

CS (90% deacetylated) was acquired from Shimakyu’s Pure Chemicals. BGE (95%) was

82

purchased from Sigma-Aldrich. Glacial acetic acid (analytical grade, 99%) was acquired from

83

Scharlau. All other reagents and solvents were commercially acquired and were used without

84

further purification. The deionized water used in all experiment had a resistivity of 18 MΩ cm.

85

Synthesis of the thermoresponsive CS derivative

86

The synthesis reaction of CS with BGE is shown in Scheme 1. CS (2 g) was dissolved

87

using 10 ml of 2% (v/v) acetic acid. It was stirred in a three-necked round-bottom flask at room

ACS Paragon Plus Environment

Environmental Science & Technology

88

temperature until all CS flakes were completely dissolved. The solution was heated under reflux

89

to 75 °C in an oil bath, followed by the addition of 1.25 M NaOH and stirred for 1 h. Four

90

formulations were prepared using various volumes of BGE: CS-BGE-1 (1 ml BGE); CS-BGE-2

91

(3 ml BGE); CS-BGE-3 (6 ml BGE); and CS-BGE-4 (9 ml BGE). The reaction was conducted

92

under continuous stirring at 75 °C. After 5 h, the mixture was cooled in an ice bath and

93

neutralized to pH 7.0 using 1 M HCl. The product was washed three times with 90% (v/v)

94

acetone. The product was placed in a dialysis bag and dialyzed in deionized water for 24 hours to

95

purify the sample. The precipitate was filtered and then dried overnight at 50 °C.

96

Characterization of the thermoresponsive chitosan derivative

97

The compounds were analyzed by total reflectance Fourier transform infrared

98

spectroscopy (ATR-FTIR) on a Perkin-Elmer Spectrum One over the wavenumber region from

99

4000 to 900 cm-1. X-ray photoelectron spectroscopy (XPS) was carried out on a Thermo

100

Scientific K-Alpha to characterize the elemental composition of the samples. LCSTs of 1 wt%

101

CS-BGE aqueous solutions were measured through turbidity measurements using a UV-vis

102

spectrophotometer (Perkin-Elmer Lambda 25) at 500 nm with a heating rate of 1 °C/min.

103

Scanning electron microscopy (SEM, Hitachi S4800) was performed to investigate the formed

104

particles. The samples were dried on a Si sample stage at 15 °C and 60 °C. The mean particle

105

size distribution at 15 °C and 60 °C was measured by dynamic light scattering (DLS) using a

106

Beckman Coulter DelsaNano S. The samples were measured for 90 s at each temperature.

107

Positron annihilation lifetime spectroscopy

108

The free volume in the 1 wt% aqueous solution of the thermoresponsive chitosan

109

derivative was measured using positron annihilation lifetime spectroscopy. A conventional fast-

ACS Paragon Plus Environment

Page 6 of 24

Page 7 of 24

Environmental Science & Technology

110

fast coincidence spectrometer with a time resolution of 250 ps was used. A radioactive source of

111

22

112

annihilation lifetimes were recorded using a fast-fast coincidence timing system. A time-to-

113

amplitude converter was used to convert the lifetimes and to store the timing signals in a multi-

114

channel analyzer (Ortec System). Two million counts were collected, and all positron

115

annihilation lifetime spectra were analyzed by a finite-term lifetime analysis method using the

116

PATFIT program. 24, 25

117

Forward osmosis and microfiltration test

Na (0.74 MBq) sealed between 12-µm-thick Kapton films was placed in the solution. Positron

118

The permeation flux was measured using small-scale U-shaped FO tubes from Narika

119

Corp. (OP-25U F35-2111). A thin-film composite membrane from Hydration Technologies, Inc.

120

(HTI) was placed and sealed between the two glass tubes. One side was filled with 0.025 wt%

121

Congo Red dye as the feed solution. The other side was filled with 1 wt% aqueous solution of

122

CS-BGE-3 as the draw solution. The temperature of the solutions was maintained at room

123

temperature during the FO tests. The water permeation flux (L/m2h) was calculated as the

124

volume change of the draw solution (L) over time (h) and effective surface area (m2) of the

125

membrane. The percent rejection (%) was calculated as the difference of concentration in feed

126

and permeate divided by the feed concentration times 100. The osmolality of the

127

thermoresponsive chitosan derivatives and Congo Red dye was measured using an osmometer

128

(model 3320 micro-osmometer, Advanced Instruments, Inc.). The draw solution was heated to

129

60 °C to separate the water from the draw solute through microfiltration at operating pressure of

130

1 bar (Gore® Microfiltration membrane, Product number: GMM-404, pore size: 0.45 µm).

131

ACS Paragon Plus Environment

Environmental Science & Technology

132

Results & Discussion

133

Modification of Chitosan

134 135

Figure 1. FTIR spectra of BGE, CS, and CS derivatives: CS-BGE-1, CS-BGE-2, CS-BGE-3 and

136

CS-BGE-4.

137

The FT-IR spectra of BGE, CS, CS-BGE-1, CS-BGE-2, CS-BGE-3 and CS-BGE-4 in

138

transmission mode are presented in Figure 1. The spectrum of BGE exhibited peaks at 2965 cm-1,

139

2940 cm-1 and 2867 cm-1, which are all attributed to alkyl –CH stretching vibrations. The peak at

140

1110 cm-1 is attributed to the C–O–C stretching of the epoxide ring. The characteristic peaks of

141

the CS were observed at 3347 cm-1 and 3310 cm-1; these bands are assigned to the broad O–H

142

and N–H stretching, respectively. The CS spectrum also showed a –CH stretching vibration 2935

143

cm-1, a strong –NH2 bending vibration at 1650 cm-1, an N–H bending vibration at 1550 cm-1, a

144

C–O–C asymmetric stretching of the glycosidic linkage at 1070 cm-1, and a C–O stretching

145

vibration at 1022 cm-1.

146

The spectra of the CS derivatives showed a broad stretching of O–H absorption at 3347

147

cm-1, which is attributed to the CS backbone. Compared with spectrum of the pristine CS, the

ACS Paragon Plus Environment

Page 8 of 24

Page 9 of 24

Environmental Science & Technology

148

spectra of the CS derivatives showed an increased band intensity for the alkyl groups (–CH

149

stretching) at 2965 cm-1, 2940 cm-1, and 2867 cm-1; this increase in intensity was due to the

150

addition of BGE. The band intensity also increased with increasing BGE content. The spectra of

151

the CS derivatives also showed weaker bands representing N–H bending absorptions at 1650 cm-

152

1

153

BGE bonded to the free amine groups of CS. The C–O–C band of the epoxide ring from BGE

154

was not observed in the spectra of the CS derivatives; however, the spectra of the CS derivatives

155

showed a shift of the C–O stretching band at 1100 cm-1, indicating that the epoxide ring was

156

opened during the reaction and bound to either the free –OH or the free –NH2 groups of the CS,

157

thereby forming an ether linkage. These results indicate that BGE was successfully grafted onto

158

the molecular chains of CS.

159

Table 1. XPS elemental analyses of CS and its derivatives.

and 1550 cm-1 as the BGE content was increased; the emergence of these bands indicates that

CS CS-BGE-1 CS-BGE-2 CS-BGE-3 CS-BGE-4

C (%) 61.64 65.56 68.29 67.67 68.87

O (%) 31.81 30.37 28.74 30.16 28.34

N (%) 6.55 4.07 2.97 2.17 1.79

N/C 0.106 0.062 0.043 0.032 0.026

160

XPS was performed to confirm changes in the elemental composition of the CS

161

derivatives prepared by the addition of BGE. Table 1 lists the elemental compositions and N/C

162

ratios of CS and its thermoresponsive derivatives. Compared to the carbon composition of the

163

unmodified CS, that of the CS derivatives increased when BGE was added. As a result, a

164

decrease in the nitrogen content was observed. These results show that upon the addition of more

165

alkyl groups, the N/C ratio decreased. This noticeable trend indicates that changes occurred in

ACS Paragon Plus Environment

Environmental Science & Technology

Page 10 of 24

166

the molecular structure due to covalent bonding of BGE to the CS backbone. Both the FTIR and

167

XPS analyses demonstrate the presence of the hydrophobic moiety on the CS derivatives.

168

Thermoresponsive solubility

169

The LCST can be identified as the initial break point,26, 29

27

as the temperature

170

corresponding to 90% transmittance28,

171

transmittance1, 9, 27 in transmittance vs. temperature curves obtained by UV-Vis spectroscopy. In

172

this study, we chose to define the LCST as the temperature corresponding to 90% transmittance.

173

The initial break point does not apply to our curves because the curve drops too rapidly. On the

174

other hand, some curves did not reach 50% transmittance.

or as the temperature corresponding to 50%

80

80

Transmittance(%)

100

Transmittance(%)

100

CS-BGE-1 0.5wt% 1wt% 1.5wt%

60

40

20

CS-BGE-2 0.5wt% 1wt% 1.5wt%

60

40

20

0

0 0

10

20

30

40

50 o

60

70

80

0

10

20

Temperature( C)

80

80

Transmittance(%)

100

Transmittance(%)

100

60

CS-BGE-3 0.5wt% 1wt% 1.5wt%

40

50 o

60

70

80

CS-BGE-4 0.5wt% 1wt% 1.5wt%

60

40

0

0 0

176

40

20

20

175

30

Temperature( C)

10

20

30

40

50 o

60

70

80

0

10

20

Temperature( C)

30

40

50 o

Temperature( C)

Figure 2. Transmittance vs. temperature curves of CS derivatives at 500 nm.

ACS Paragon Plus Environment

60

70

80

Page 11 of 24

Environmental Science & Technology

177

Zhang et al. previously used thermoresponsive 2-hydroxy-3-butoxypropyl starch (i.e.,

178

starch molecules grafted with BGE) to demonstrate that the LCST behavior of the starch changed

179

with changes in molar substitution.1, 9 Figure 2 shows the transmittance vs. temperature curves

180

of the modified CS derivatives with various BGE contents and different aqueous concentrations.

181

LCST behavior is observed from the temperature where the solution is clear showing high

182

transmittance up to the temperature where the solutions turns into a turbid solution exhibiting

183

low transmittance. Neither CS-BGE-1 nor CS-BGE-2 exhibited temperature-dependent light

184

transmittance. These results are attributed to the low extent of BGE addition to the amine groups

185

of the CS, as confirmed by the FTIR spectra. However, CS-BGE-3 and CS-BGE-4 exhibited

186

temperature-dependent light transmittance, even at different concentrations of the aqueous

187

solutions. These results demonstrate that sufficient amounts of hydrophobic reagents must be

188

added to the mixture to observe the LCST behavior. We also observed that lowering the polymer

189

concentration increases the LCST. The 0.5 wt% solutions of CS-BGE-3 and CS-BGE-4 did not

190

reach transmittances lower than ~80% and ~90%, respectively. This is due to the few particles

191

formed by the presence of low solute. The particles will take time to aggregate and show a very

192

slow LCST behavior. Thus a less turbid solution is observed with high transmittance. CS-BGE-3

193

exhibited the best observable thermoresponsive behavior among the investigated formulations, as

194

demonstrated by its sharp phase transition near ambient temperature. With an increase in the

195

BGE content, the number of hydrophobic groups on the CS derivatives increased, which

196

disrupted the inter- and intramolecular hydrogen bonds of the CS backbone. The excessive

197

disruption of hydrogen bonds resulted in a reduced thermoresponsive effect.

ACS Paragon Plus Environment

Environmental Science & Technology

198

Page 12 of 24

(b)

(a)

199

Figure 3. (a) Transmittance vs. temperature curves of CS-BGE-3 at different concentrations. (b)

200

The effect of concentration on LCST and ∆T1/2.

201

CS-BGE-3 was further characterized for its phase-transition behavior. Figure 3a displays

202

the effect of polymer concentration on the phase-transition behavior. Polymer solutions with

203

concentrations from 0.5 wt% to 2 wt% exhibited different LCST ranges. Solutions with lower

204

polymer concentrations exhibited higher LCSTs and broader phase transitions. With decreasing

205

polymer concentration, the light transmittance of the solutions decreased. This result is attributed

206

to the presence of less solute and insufficient polymer to aggregate and form a completely white

207

turbid solution, unlike the solutions with higher polymer concentrations. A sharp phase transition

208

is important for thermoresponsive smart materials. The microcalorimetric endotherm (∆T1/2),

209

which is the half-value of the temperature difference between the final and initial break points in

210

the transmittance vs. temperature curves, was used to better evaluate the sharpness of the phase

211

transitions.27 Figure 3b shows that the phase transition of the 0.5 wt% solution was broad and

212

that its ∆T1/2 was 19.5 °C. When the polymer concentration was increased to 2 wt%, the phase

213

transition became sharper, with a ∆T1/2 of 5.1 °C. This result can be explained by the effect of the

ACS Paragon Plus Environment

Page 13 of 24

Environmental Science & Technology

214

polymer concentration on the time required for aggregation.9 That is, when the polymer

215

concentration is low, additional time is needed to form aggregates.

216

Thermoresponsive behavior of CS derivatives (a) (b)

217 218

Figure 4. (a) Digital photographs of 1 wt% CS-BGE-3 aqueous solution at 15 °C and 60 °C,

219

along with corresponding SEM images of the particles. (b) Reversible changes in the mean

220

particle size of CS-BGE-3 aqueous solution at 15 °C and 60 °C.

221

We observed that the 1 wt% CS-BGE-3 solution turned turbid when heated beyond its

222

LCST and was able to return to its original state when cooled below its LCST (Figure 4a). This

223

observation reveals that the aqueous solution exhibits reversible thermoresponsiveness. The

224

SEM images reveal that particles were formed in the solution. The size of particles obtained by

225

drying the solution at 15 °C was approximately 10 µm, whereas that of particles obtained from

226

drying the solution at 60 °C was approximately 30 µm. The SEM images further show that the

227

particles were uniformly dispersed and that aggregates formed at higher temperatures. A similar

228

trend was reported on the basis of TEM images of a thermoresponsive cellulose ether.2

ACS Paragon Plus Environment

Environmental Science & Technology

Page 14 of 24

229

To thoroughly investigate the size of the particle and aggregation with respect to temperature

230

changes, dynamic light scattering (DLS) measurements were performed at 15 °C and 60 °C

231

(Figure 4b). The sample was analyzed at 15 °C for 90 s. The temperature of the sample was then

232

increased to 60 °C and analyzed for another 90 s. This test was repeated for three temperature

233

cycles. Interestingly, the mean particle size at 15 °C ranged from approximately 1100 nm to

234

1300 nm, whereas that at 60 °C initially ranged from 3000 nm and then abruptly increased with

235

time to approximately 4250–4750 nm. The size observed in the SEM images correlates with the

236

DLS results. Notably, the particle size at 60 °C continually increased with time, demonstrating

237

that the particles continued to aggregate. A possible reason for this behavior is the continued

238

disruption of the inter- and intramolecular hydrogen bonds in the polymer. The CS derivative has

239

an amphiphilic nature; thus, the hydrophobic groups from the hydrophobic reagent bonded onto

240

the CS chain provide a means for the molecule to form particles in solution.

241

Microstructure analysis of the thermoresponsive property by positron annihilation lifetime

242

spectroscopy

243

(a)

(b)

ACS Paragon Plus Environment

Page 15 of 24

Environmental Science & Technology

244

Figure 5. Positron annihilation lifetime spectroscopy analysis for 1 wt% CS-BGE-3 aqueous

245

solution at 15 °C and 60 °C. Reversible thermoresponsive behavior effect on (a) o-Ps lifetime

246

and free-volume size and (b) o-Ps intensity.

247

Positron annihilation lifetime spectroscopy (PALS) is a highly sensitive technique for

248

monitoring conformational, structural and microenvironmental transformations arising from

249

subtle geometric changes in the molecular geometry of polymers.30-34 Quantitative analysis of the

250

free-volume size and the free-volume size distribution for the thermoresponsive polymeric

251

aqueous solutions were determined by the PALS technique for the first time. Figure 5 shows the

252

o-Ps lifetime and o-Ps intensity of a 1 wt% CS-BGE-3 solution. The o-Ps lifetime is related to

253

the free-volume that is available between polymer chains. A longer o-Ps lifetime corresponds

254

with free-volumes with larger radii. As evident in Figure 5a, the free-volume size of the solution

255

was larger at lower temperatures than when heated to higher temperatures. At 15 °C, the o-Ps

256

lifetime was high at approximately 3.8–4.0 ns, corresponding to radii between 4.02 and 4.24 Å.

257

When the solution temperature was increased to 60 °C, the o-Ps lifetime decreased substantially

258

to 2.1–2.4 ns, corresponding to radii between 2.86 and 3.20 Å. The temperature was then cycled.

259

These experiments show that the particles at 15 °C exhibit a larger free-volume than those at 60

260

°C, suggesting a reversible thermoresponsiveness. Next, we monitored the o-Ps intensities,

261

shown in Figure 5b, to assess the available free-volume. Large o-Ps intensity values indicate

262

large amounts of free-volume holes. A similar trend was observed at 15 °C, where the intensity

263

is higher, indicating approximately 21–22% free-volume. However, when the temperature was

264

increased to 60 °C, the o-Ps intensity decreased to approximately 10–12%. The data also show

265

the reversibility of the free-volume. These results suggest that at low temperatures, the

266

hydrophobic part of the CS derivative is hidden within the well-dispersed particles. By contrast,

ACS Paragon Plus Environment

Environmental Science & Technology

Page 16 of 24

267

at high temperatures, the polymer chains tend to rearrange to expose the hydrophobic moiety and

268

aggregate, which leads to smaller free-volume holes. These events explain the dramatic changes

269

in the o-Ps lifetime and o-Ps intensity during the phase transition. A better representation of this

270

idea is shown in Scheme 1. At temperatures below the LCST, the polymer chains are linear and

271

form hydrogen bonds with water molecules, resulting in larger free-volume spaces. During the

272

transition at temperatures greater than the LCST, the polymer chains tend to fold and rearrange.

273

In this phase, the hydrogen bonds decrease, and the free-volume spaces shrink.

274

Thermoresponsive chitosan derivative as a draw solute 800

Osmolality (mOsm)

700 600 500 400 300

CS-BGE-1 CS-BGE-2 CS-BGE-3 CS-BGE-4

200 100 0

275

congo 0.0 red dye

0.5

1.0

1.5

2.0

Concentration (wt%)

276

Figure 6. Osmolality of Congo Red dye and different concentrations of CS derivatives aqueous

277

solution.

278

Current challenges in FO involve the development of good draw solutes. In this study, we

279

used a simple FO setup to initially study the potential of the thermoresponsive CS-BGE-3

280

derivative as a draw solute. The osmolality of the Congo Red dye and different concentrations of

281

CS derivatives aqueous solution was evaluated; the results are shown in Figure 6. The

282

osmolality of the dye was lower than that of the thermoresponsive CS derivative at different

ACS Paragon Plus Environment

Page 17 of 24

Environmental Science & Technology

283

concentrations in aqueous solutions. The lower BGE content resulted to a higher osmolality.

284

However, these CS derivatives with low BGE content do not exhibit LCST behavior. Notably,

285

the osmolality of the best thermoresponsiveness at 1 wt% CS-BGE-3 (492 mOsm) was higher

286

than that of the dye (133 mOsm). Thus, a 0.025 wt% Congo Red dye solution was used as the

287

feed solution and 1 wt% CS-BGE-3 as the draw solution. A commercial FO membrane was used.

288

The experiment was performed at room temperature, which is below the LCST of the 1 wt% CS-

289

BGE-3 solution.

290 291

Figure 7. Simple FO test for 1 wt% CS-BGE-3 as draw solute and microfiltration recovered CS

292

derivatives. Feed solution: 0.025 wt% Congo Red dye.

293

Figure 7 shows the setup used for FO and microfiltration. Initially, an equal volume of

294

both the feed and draw solutions were placed on either side of a commercial FO membrane. The

295

ability of the draw solute to draw water from the feed solution was initially investigated using

296

deionized water as the feed solution. The flux was 9.1 L/m2h and CS derivative rejection 99.8 %.

297

In the case of dye dehydration, a 10 cm difference in height was observed between the feed and

298

draw solutions after a period of time. The calculated flux was 8.6 L/m2h and CS derivative

299

rejection 99.8 %, indicating good permeation and negligible solute back diffusion. The small

ACS Paragon Plus Environment

Environmental Science & Technology

Page 18 of 24

300

particles may have enhanced the drawability of the solution because they are more hydrophilic.

301

The water from the draw solution was collected and heated to 60 °C, a temperature above its

302

LCST. The CS derivative aggregation can facilitate separation of the particles via microfiltration

303

(pore size 1.0 µm), 99.9 % was recovered enabling the particles to be reused (See Figure 7.

304

right). We followed the ISO 10993-535 method for CSBGE-3 cytotoxicity test. The CSBGE-3

305

was extracted for cell culture. Results showed a cell survival of 92% and it has been determined

306

to be zero-grade (non-toxic). The synthesized thermoresponsive CS derivative showed potential

307

to be used as a draw solute in the FO process.

308

In conclusion, a thermoresponsive CS derivative, CS-BGE, was synthesized from

309

hydrophilic CS reacted with hydrophobic BGE. The successful addition of BGE functional

310

groups was confirmed by FTIR spectroscopy and XPS elemental analysis. These experiments

311

showed that BGE was bound to both the amine and the hydroxyl reactive groups of the CS.

312

Varying the BGE content changed the LCST range, and the CS-BGE-3 formulation was

313

observed to exhibit the best response via a turbidity test by UV-vis spectroscopy. Increasing the

314

concentration of the thermoresponsive CS aqueous solution led to a decrease in the LCST. This

315

change was due to aggregation of more particles in solution with increasing temperature. SEM

316

images showed the aggregation of particles from 15 °C to 60 °C. A similar trend was observed

317

for the mean particle size determined by DLS; particles aggregated when the temperature was

318

increased. When the temperature was increased to 60 °C, the mean particle size continually

319

increased within 90 s and returned to a smaller size when the temperature was lowered back to

320

15 °C. Interestingly, the PALS data also showed the reversibility of the particle formation. The

321

free-volume sizes at lower temperatures was larger than those at higher temperatures. These

322

results demonstrate that changes in the microstructures occurred during the phase transition.

ACS Paragon Plus Environment

Page 19 of 24

Environmental Science & Technology

323

Furthermore, the thermoresponsive CS derivative was found to be non-toxic with 92% cell

324

survival. The results of simple FO tests suggest that the synthesized thermoresponsive CS

325

derivative can potentially be used as a draw solute because it gives a flux of 8.6 L/m2h and

326

rejection of 99.8 % upon dye dehydration.

327

Corresponding Author

328

*E-mail: [email protected]

329

Acknowledgements

330

The authors wish to sincerely thank the Ministry of Science and Technology of Taiwan for

331

financially supporting this work.

332

References

333

1.

Ju, B. Z.; Yan, D. M.; Zhang, S. F., Micelles self-assembled from thermoresponsive 2-

334

hydroxy-3-butoxypropyl starches for drug delivery. Carbohydr. Polym. 2012, 87, (2),

335

1404-1409.

336

2.

flocculation behavior for organic dye removal. Carbohydr. Polym. 2016, 136, 1209-1217.

337 338

Tian, Y.; Ju, B. Z.; Zhang, S. F.; Hou, L. N., Thermoresponsive cellulose ether and its

3.

Zhao, Q. P.; Chen, N. P.; Zhao, D. L.; Lu, X. M., Thermoresponsive Magnetic

339

Nanoparticles for Seawater Desalination. ACS Appl. Mater. Interfaces 2013, 5, (21),

340

11453-11461.

341

4.

Zhong, Y. J.; Feng, X. S.; Chen, W.; Wang, X. B.; Huang, K. W.; Gnanou, Y.; Lai, Z. P.,

342

Using UCST Ionic Liquid as a Draw Solute in Forward Osmosis to Treat High-Salinity

343

Water. Environ. Sci. Technol. 2016, 50, (2), 1039-1045.

ACS Paragon Plus Environment

Environmental Science & Technology

344

5.

Kim, J. J.; Kang, H.; Choi, Y. S.; Yu, Y. A.; Lee, J. C., Thermo-responsive oligomeric

345

poly(tetrabutylphosphonium styrenesulfonate)s as draw solutes for forward osmosis (FO)

346

applications. Desalination 2016, 381, 84-94.

347

6.

Zhao, D. L.; Wang, P.; Zhao, Q. P.; Chen, N. P.; Lu, X. M., Thermoresponsive copolymer-

348

based draw solution for seawater desalination in a combined process of forward osmosis

349

and membrane distillation. Desalination 2014, 348, 26-32.

350

7.

Li, D.; Zhang, X. Y.; Yao, J. F.; Simon, G. P.; Wang, H. T., Stimuli-responsive polymer

351

hydrogels as a new class of draw agent for forward osmosis desalination. Chem. Commun.

352

2011, 47, (6), 1710-1712.

353

8.

behavior of polymers in aqueous solution. Macromolecules 2005, 38, (24), 10155-10163.

354 355

Van Durme, K.; Rahier, H.; Van Mele, B., Influence of additives on the thermoresponsive

9.

Ju, B. Z.; Cao, S. Q.; Zhang, S. F., Effect of Additives on the Cloud Point Temperature of

356

2-Hydroxy-3-isopropoxypropyl Starch Solutions. J. Phys. Chem. B 2013, 117, (39), 11830-

357

11835.

358

10.

Jayakumar, R.; Nagahama, H.; Furuike, T.; Tamura, H., Synthesis of phosphorylated

359

chitosan by novel method and its characterization. Int. J. Biol. Macromol. 2008, 42, (4),

360

335-339.

361

11.

Jiang, M. Y.; Wang, K. M.; Kennedy, J. F.; Nie, J.; Yu, Q. A.; Ma, G. P., Preparation and

362

characterization of water-soluble chitosan derivative by Michael addition reaction. Int. J.

363

Biol. Macromol. 2010, 47, (5), 696-699.

364 365

12.

Elimelech, M.; Phillip, W. A., The Future of Seawater Desalination: Energy, Technology, and the Environment. Science 2011, 333, (6043), 712-717.

ACS Paragon Plus Environment

Page 20 of 24

Page 21 of 24

366

Environmental Science & Technology

13.

Osmosis: Modeling and Experiments. Environ. Sci. Technol. 2010, 44, (13), 5170-5176.

367 368

14.

15.

16.

17.

Chung, T.-S.; Zhang, S.; Wang, K. Y.; Su, J.; Ling, M. M., Forward osmosis processes: Yesterday, today and tomorrow. Desalination 2012, 287, 78-81.

375 376

Cath, T. Y.; Childress, A. E.; Elimelech, M., Forward osmosis: Principles, applications, and recent developments. J. Membr. Sci. 2006, 281, (1–2), 70-87.

373 374

Gray, G. T.; McCutcheon, J. R.; Elimelech, M., Internal concentration polarization in forward osmosis: role of membrane orientation. Desalination 2006, 197, (1–3), 1-8.

371 372

Zhao, S. F.; Zou, L.; Tang, C. Y. Y.; Mulcahy, D., Recent developments in forward osmosis: Opportunities and challenges. J. Membr. Sci. 2012, 396, 1-21.

369 370

Phillip, W. A.; Yong, J. S.; Elimelech, M., Reverse Draw Solute Permeation in Forward

18.

Yip, N. Y.; Tiraferri, A.; Phillip, W. A.; Schiffman, J. D.; Elimelech, M., High

377

Performance Thin-Film Composite Forward Osmosis Membrane. Environ. Sci. Technol.

378

2010, 44, (10), 3812-3818.

379

19.

Developments, challenges, and prospects for the future. J. Membr. Sci. 2013, 442, 225-237.

380 381

20.

21.

Long, Q.; Qi, G.; Wang, Y., Evaluation of renewable gluconate salts as draw solutes in forward osmosis process. ACS Sustainable Chem. Eng. 2015, 4, (1), 85-93.

384 385

Long, Q.; Wang, Y., Novel carboxyethyl amine sodium salts as draw solutes with superior forward osmosis performance. AlChE J. 2016, 62, 1226-1235.

382 383

Ge, Q.; Ling, M.; Chung, T.-S., Draw solutions for forward osmosis processes:

22.

Ling, M. M.; Wang, K. Y.; Chung, T.-S., Highly Water-Soluble Magnetic Nanoparticles as

386

Novel Draw Solutes in Forward Osmosis for Water Reuse. Ind. Eng. Chem. Res. 2010, 49,

387

(12), 5869-5876.

ACS Paragon Plus Environment

Environmental Science & Technology

388

23.

Liu, Z.; Bai, H.; Lee, J.; Sun, D. D., A low-energy forward osmosis process to produce drinking water. Energy Environ. Sci. 2011, 4, (7), 2582-2585.

389 390

Page 22 of 24

24.

Huang, Y.-H.; Chao, W.-C.; Hung, W.-S.; An, Q.-F.; Chang, K.-S.; Huang, S.-H.; Tung,

391

K.-L.; Lee, K.-R.; Lai, J.-Y., Investigation of fine-structure of polyamide thin-film

392

composite membrane under swelling effect by positron annihilation lifetime spectroscopy

393

and molecular dynamics simulation. J. Membr. Sci. 2012, 417–418, 201-209.

394

25.

Package, P., Riso National Laboratory. Roskide, Denmark 1989.

395

26.

Haba, Y.; Harada, A.; Takagishi, T.; Kono, K., Rendering poly(amidoamine) or

396

poly(propylenimine) dendrimers temperature sensitive. J. Am. Chem. Soc. 2004, 126, (40),

397

12760-12761.

398

27.

Liu, X. Y.; Cheng, F.; Liu, H. J.; Chen, Y., Unusual salt effect on the lower critical solution

399

temperature of hyperbranched thermoresponsive polymers. Soft Matter 2008, 4, (10), 1991-

400

1994.

401

28.

polyethers. J. Am. Chem. Soc. 2006, 128, (25), 8144-8145.

402 403

Jia, Z. F.; Chen, H.; Zhu, X. Y.; Yan, D. Y., Backbone-thermoresponsive hyperbranched

29.

Xia, Y.; Yin, X. C.; Burke, N. A. D.; Stover, H. D. H., Thermal response of narrow-

404

disperse poly(N-isopropylacrylamide) prepared by atom transfer radical polymerization.

405

Macromolecules 2005, 38, (14), 5937-5943.

406

30.

Liao, K.-S.; Chen, H.; Awad, S.; Yuan, J.-P.; Hung, W.-S.; Lee, K.-R.; Lai, J.-Y.; Hu, C.-

407

C.;

Jean,

Y.,

Determination

of

free-volume

408

orthopositronium

components

in

positron

409

Macromolecules 2011, 44, (17), 6818-6826.

properties

annihilation

ACS Paragon Plus Environment

in

polymers

lifetime

without

spectroscopy.

Page 23 of 24

410

Environmental Science & Technology

31.

Hung, W.-S.; De Guzman, M.; Huang, S.-H.; Lee, K.-R.; Jean, Y.; Lai, J.-Y.,

411

Characterizing free volumes and layer structures in asymmetric thin-film polymeric

412

membranes in the wet condition using the variable monoenergy slow positron beam.

413

Macromolecules 2010, 43, (14), 6127-6134.

414

32.

Chen, H.; Hung, W.-S.; Lo, C.-H.; Huang, S.-H.; Cheng, M.-L.; Liu, G.; Lee, K.-R.; Lai,

415

J.-Y.; Sun, Y.-M.; Hu, C.-C., Free-volume depth profile of polymeric membranes studied

416

by positron annihilation spectroscopy: layer structure from interfacial polymerization.

417

Macromolecules 2007, 40, (21), 7542-7557.

418

33.

Tung, K.-L.; Jean, Y.-C.; Nanda, D.; Lee, K.-R.; Hung, W.-S.; Lo, C.-H.; Lai, J.-Y.,

419

Characterization of multilayer nanofiltration membranes using positron annihilation

420

spectroscopy. J. Membr. Sci. 2009, 343, (1), 147-156.

421

34.

Huang, S.-H.; Hung, W.-S.; Liaw, D.-J.; Tsai, H.-A.; Jiang, G. J.; Lee, K.-R.; Lai, J.-Y.,

422

Positron annihilation study on thin-film composite pervaporation membranes: Correlation

423

between polyamide fine structure and different interfacial polymerization conditions.

424

Polymer 2010, 51, (6), 1370-1376.

425 426

35.

Wallin, R. F.; Arscott, E., A practical guide to ISO 10993-5: Cytotoxicity. Med. Device Diagn. Ind. 1998, 20, 96-98.

427 428

ACS Paragon Plus Environment

Environmental Science & Technology

429

Page 24 of 24

Table of Contents Graphic

430 431

Reaction between chitosan and butyl glycidyl ether, producing a thermoresponsive chitosan

432

derivative; the photographs show particles exhibiting lower critical solution temperature

433

behavior.

ACS Paragon Plus Environment