Việt Nam là nước nông nghiệp, sản xuất nhiều gạo và sản phẩm phụ là trấu. Trấu được
xem là chất thải nông nghiệp và được đốt bỏ. Quá trình này gây ô nhiễm môi trường, thu hút
nhiều nghiên cứu để tận dụng trấu. Nhóm nghiên cứu ở bộ môn Ceramic tận dụng trấu như
nguồn cung cấp silica (SiO2). Cần nhấn mạnh rằng thành phần chính của trấu là silica.
Nghiên cứu này công bố kỹ thuật mới phối trộn tro và CaO với tỷ lệ mol Ca/Si 1.0 để tổng
hợp khoáng xonotlite như vật liệu môi trường. Ưu điểm của nghiên cứu này là tận dụng
nguồn trấu Việt Nam và giảm tác hại lên môi trường bằng phản ứng thủy nhiệt.
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Mạc Xuân Hòa, Nguyễn Lâm Nhu, Nguyễn Thị Hồng Hạnh
66
16. Wong Y.-M. and Siow L.-F. - Effects of heat, pH, antioxidant, agitation and light on
betacyanin stability using red-fleshed dragon fruit (Hylocereus polyrhizus) juice and
concentrate as models, Journal of Food Science and Technology 52 (2015) 3086-3092.
ABSTRACT
COMPARISON OF MICROWAVE AND ULTRASOUND-ASSISTED EXTRACTION
FOR LEACHING BETACYANIN FROM DRAGON FRUIT PEELS
Mac Xuan Hoa, Nguyen Lam Nhu, Nguyen Thi Hong Hanh*
Ho Chi Minh City University of Food Industry
*Email: hanhnguyen300995@gmail.com
Extraction of betacyanin from dragon fruit peels by microwave and ultrasound was
studied by experimental method. In both microwave and ultrasound-assisted extractions,
effects of extraction time (10-110 sec for microwave; 5-25 min for ultrasound) and different
powers (200 W, 400 W, 600 W for microwave; 150 W, 187.5 W, 225 W for ultrasound) were
investigated. In microwave-assisted extraction, the highest betacyanin (0.456 mg/100 g) was
obtained in 30 sec and 600 W powers. For ultrasound-assisted extraction, the condition
which acquired the highest betacyanin (0.409 mg/100 g) was 10 min and 187.5 W powers.
Microwave reduced extraction time by 95% and betacyanin obtained in this method was
higher (0.456 mg/100 g) compaired with (0.409 mg/100 g).
Key words: Microwave, ultrasound, betacyanin, dragon fruit peels.
Tạp chí Khoa học công nghệ và Thực phẩm 12 (1) (2017) 67-72
SYNTHESIS OF CALCIUM SILICATE HYDRATE (CSH) FROM
VIETNAM RICE HUSH
1* 1 1 2Pham Trung Kien , Phan Viet Hoang , Huynh Dai Phu , Nguyen Van Tam ,
2 3 4Ngo Vo Ke Thanh , Nguyen Hoc Thang , Hirofumi Hinode
1Ho Chi Minh City University of Technology (HCMUT)
2Research Laboratories Center Saigon Hi-Tech Park
3Ho Chi Minh City University of Food Industry (HUFI),
4Tokyo Institute of Technology
*Email: phamtrungkien@hcmut.edu.vn
Received: 25 June 2017; Accepted for publication: 12 September 2017
ABSTRACT
Vietnam is an agricultural country, which produces lot of rice and its by product is rice
husk ash (RHA). The RHA is considered as waste in agriculture, and treated by burn in the
open air. This process causes air pollution, thus attracted Vietnamese researchers to find
alternative method to reduce the impact of rice husk ash on environment. The research group
in Department of Ceramic Materials aims to reuse rice husk ash as source of silica (SiO2). It
needs to emphasize that the main content of rice husk ash is silica. This research reports new
technology to mixing RHA and CaO with the Ca/Si molar ratio of 1.0, in order to synthesize
calcium silicate hydrate (CSH) such as tobermorite (C5S6H5) and xonotlite (C6S6H) as
environmental materials. The advantage of our study is to utilize the Vietnam RHA and to
reduce the environmental impacts by using hydrothermal treatment technique.
Key words: Calcium silicate hydrate, rice hush ash, hydrothermal treatment, ceramic.
1. INTRODUCTION
Vietnam is an agricultural country, which produces lot of rice and its by product is rice
husk ash (RHA). The RHA is considered as waste in agriculture, and treated by burn in the
open air. This process causes air pollution, thus attracted researchers to find alternative
method to reduce the impact of rice husk ash on environment [1-3]. The research group in
Department of Ceramic Materials aims to reuse rice husk ash as source of Silica (SiO2) [4-8].
The obtained silica can be used as stating materials to reaction with calcium source to form
calcium silicate hydrate (CSH). By this chemical reaction, we can utilize the Vietnam rice
hush for sustainable development.
2. METHODOLOGY
Preparation of Vietnam Rice Husk Ash (VRH): Rice husk is burned at 600 oC with the
heating rate of 10 oC/min (Naberthem 1400, Nabertherm, Germany), then soaking for 4
hours to complete burning. The phase composition of obtained VRHA is characterized using
X-ray Diffraction (XRD) and Fourier transform infrared spectroscopy (FTIR). The chemical
composition of VRHA is analyzed using X-Ray Fluorescent (XRF) method.
Preparation of CaO: CaO is used from the commercial without purified (Xilong
67
Pham Trung Kien, Huynh Dai Phu, Nguyen Van Tam, Ngo Vo Ke Thanh,
68
Chemical, China). The phase composition of commercialized CaO using XRD.
Hydrothermal treatment the mixture of VRHA and CaO: The mixture of VRHA and
CaO is mixed with the Ca/P molar ratio of 1.0 with the moisture of 10% (weight percent)
then pressing at 30 MPa to form the compact disk with diameter of 9 mm. The compacted
cylinder is hydrothermally treated at different temperature levels for 24 hours to obtain
calcium silicate hydrate such as tobermorite and xonotlite.
Phase analysis: The powder X-ray Diffraction (XRD) patterns of disk samples were
recorded with a vertically mounted diffractometer system (Bruker-AXS: D8 ADVANCE,
Germany) using Ni filtered CuKa generated at 40 Kv, 20 mA.
The chemical compositions of sample were characterized by XRF (ZSX, Rigaku,
Japan) operated at 40 kV and 40 mA.
The bonding chemical of sample was characterized by FTIR analysis: the sample were
ground into fine powder, mixed with KBr powder at the ratio 1:200. Infrared spectra were
measured at a resolution of 2 cm-1 using a Fourier transform infrared (FTIR) spectrometer
(PerkinElmer 2000, USA).
3. RESULTS AND DISCUSSIONS
The chemical composition of RHA is shown in Table 1:
Table 1. The chemical composition of RHA (weight percent)
SiO2 K2O CaO P2O5 MgO Al2O3 MnO Fe2O3 SO3 other
LOI Total
92.7 3.16 1.33 0.596 0.466 0.306 0.291 0.242 0.126 0.153
0.63 100
The phase analysis of VRHA is given in Figure 1, indicating that VRHA is composed
of crystabalite, which shows the peak at 22o (PDF# 01-082-0512).
Figure 1. XRD pattern of VRHA
5 10 15 20 25 30 35 40 45 50 55 60
Int
en
sit
y /
ar
b.
un
it
2theta / degree
Int
en
sit
y /
ar
b.
un
it
Pham Trung Kien, Huynh Dai Phu, Nguyen Van Tam, Ngo Vo Ke Thanh,
68
Chemical, China). The phase composition of commercialized CaO using XRD.
Hydrothermal treatment the mixture of VRHA and CaO: The mixture of VRHA and
CaO is mixed with the Ca/P molar ratio of 1.0 with the moisture of 10% (weight percent)
then pressing at 30 MPa to form the compact disk with diameter of 9 mm. The compacted
cylinder is hydrothermally treated at different temperature levels for 24 hours to obtain
calcium silicate hydrate such as tobermorite and xonotlite.
Phase analysis: The powder X-ray Diffraction (XRD) patterns of disk samples were
recorded with a vertically mounted diffractometer system (Bruker-AXS: D8 ADVANCE,
Germany) using Ni filtered CuKa generated at 40 Kv, 20 mA.
The chemical compositions of sample were characterized by XRF (ZSX, Rigaku,
Japan) operated at 40 kV and 40 mA.
The bonding chemical of sample was characterized by FTIR analysis: the sample were
ground into fine powder, mixed with KBr powder at the ratio 1:200. Infrared spectra were
measure at a resolution of 2 cm-1 using a Fourier transform infrared (FTIR) spectrometer
(PerkinElmer 2000, USA).
3. RESULTS AND DISCUSSIONS
The chemical composition of RHA is shown in Table 1:
Table 1. The chemical composition of RHA (weight percent)
SiO2 K2O CaO P2O5 MgO Al2O3 MnO Fe2O3 SO3 other
LOI Total
92.7 3.16 1.33 0.596 0.466 0.306 0.291 0.242 0.126 0.153
0.63 100
The phase analysis of VRHA is given in Figure 1, indicating that VRHA is composed
of crystabalite, which shows the peak at 22o (PDF# 01-082-0512).
Figure 1. XRD pattern of VRHA
5 10 15 20 25 30 35 40 45 50 55 60
Int
en
sit
y /
ar
b.
un
it
2theta / degree
Int
en
sit
y /
ar
b.
un
it
Synthesis of calcium silicate hydrate (CSH) from Vietnam rice hush
69
The FTIR of VRHA is given in Figure 2, indicating that the main chemical bonding of
VRHA is O-Si-O, go well with XRD data given in Figure 1.
Figure 2. FTIR spectrum of VRHA
The phase analysis of CaO is given in Figure 3, indicating that commercialized CaO is
puried (which the peak of CaO at 32o, 37o and 54o corresponding to PDF# 01-077-2376) and
can be used for further reaction.
Figure 3. XRD pattern of CaO
The phase analysis of mixture of VRHA/CaO before and after hydrothermal treatment
at 110 oC, and 200 oC for 24 hours.
Before hydrothermal treatment, the phase composition of sample is crystobalite and
Ca(OH)2. The present of Ca(OH)2 is given by hydration of CaO and water during the mixing
process. After hydrothermal treatment, we can observe the new phase of Calcium Silicate
Hydrate (CSH), Tobermorite (at 110 oC for 24 hours) and Xonotlite (at 200 oC for 24 hours).
The morphology of sample before and after hydrothermal treatment at 110 oC and 200 oC for
24 hours also is given at Figure 5.
5 10 15 20 25 30 35 40 45 50 55 60
Int
en
sit
y /
ar
b.
un
it
2theta / degree
Int
en
sit
y /
ar
b.
un
it
Pham Trung Kien, Huynh Dai Phu, Nguyen Van Tam, Ngo Vo Ke Thanh,
70
Figure 4. XRD pattern of mixture of VRHA/CaO before and after hydrothermal
treatment at different temperature levels: (a) before; (b) 110 oC to obtain Tobermorite;
and (c) 200 oC to obtain Xonotlite.
We can observe the morphological change of sample before and after hydrothermal
treatment with the increase of hydrothermal treatment temperature. At 110 oC and 200 oC,
we can observe the new pore, while the morphology transitionally changes from polyonal-
like shape to needle-like shape and these needle-like shape crystals are interlocked together
(Figure 5c). The size of new needle-like shape also increased with the increase of
hydrothermal treatment temperature (Figure 5b, 5c).
Figure 5. SEM images of sample before and after hydrothermal treatment at different
temperature levels: (a) before; (b) 110 oC; and (e) 200 oC.
50
Before
110oC, 24h
200oC, 24h
Tobermorite
Xonotlite
Ca/Si 1.0 a)
b)
c)
a) Before
b) 110oC/24h c) 200oC/24h
10m
10m10m
Pham Trung Kien, Huynh Dai Phu, Nguyen Van Tam, Ngo Vo Ke Thanh,
70
Figure 4. XRD pattern of mixture of VRHA/CaO before and after hydrothermal
treatment at different temperature levels: (a) before; (b) 110 oC to obtain Tobermorite;
and (c) 200 oC to obtain Xonotlite.
We can observe the morphological change of sample before and after hydrothermal
treatment with the increase of hydrothermal treatment temperature. At 110 oC and 200 oC,
we can observe the new pore, while the morphology transitionally changes from polyonal-
like shape to needle-like shape and these needle-like shape crystals are interlocked together
(Figure 5c). The size of new needle-like shape also increased with the increase of
hydrothermal treatment temperature (Figure 5b, 5c).
Figure 5. SEM images of sample before and after hydrothermal treatment at different
temperature levels: (a) before; (b) 110 oC; and (e) 200 oC.
50
Before
110oC, 24h
200oC, 24h
Tobermorite
Xonotlite
Ca/Si 1.0 a)
b)
c)
a) Before
b) 110oC/24h c) 200oC/24h
10m
10m10m
Synthesis of calcium silicate hydrate (CSH) from Vietnam rice hush
71
4. CONCLUSIONS
By using hydrothermal treatment of the compaction of VRA and CaO with the molar
ratio of Ca/Si 1.0, we can synthesize Tobermorite (C5S6H5) at 110 oC and Xonotlite (C6S6H)
at 200 oC. Both Tobermorite and Xonotlite are calcium silicate hydrate, and can be used as
environmental materials. Thus, this research can contribute to the sustainability of Vietnam
rice hush industry.
ACKNOWLEDGEMENTS
The research group would like to thank the Ho Chi Minh City University of Technology
(HCMUT-VNU), and Department of International Engineering Development (Tokyo Institute
of Technology), HUFI for supporting the research facilities. Thanks also go to the R&D Saigon
Hi Tech Park (SHTP) the organization supported the financial aid for this study.
REFERENCES
1. Tiggemann M. H., Tomacheski D., Celso F., Ribeiro V. F., Nachtigall S. M. B. - Use
of wollastonite in a thermoplastic elastomer composition, Polymer Testing 32 (2013)
1373–1378.
2. Soliman A. M., Nehdi M. L. - Effects of shrinkage reducing admixture and
wollastonite microfiber on early-age behavior of ultra-high performance concrete,
Cement & Concrete Composites 46 (2014) 81–89.
3. Saadaldin S., Rizkalla A. - Synthesis and characterization of wollastonite glass–
ceramics for dental implant applications, Dental Materials 30 (2014) 364-371.
4. Pham Trung Kien, Nguyen Hoc Thang, Do Quang Minh, Do Minh Hien, S. M.
Gallardo, F. T. Bacani, Hirofumi Hinode, Michael Angelo B. Promentilla. -
Properties and microstructure of geopolymer from red mud, rice husk ash and
diatomite, Journal of Science and Technology 53 (2B) (2015) 215-221.
5. Michael Angelo B. Promentilla , Nguyen Hoc Thang, Pham Trung Kien, Hirofumi
Hinode, Florinda T. Bacani, Susan M. Gallardo. - Optimizing ternary-blended
geopolymers with multi-response surface analysis, Waste and Biomass Valorization
7 (29) (2016) 1-11.
6. Pham TK, Kieu DTK, Do QM, Nguyen HT, Ly HA, Pham TTT. - Research on
wasted glass as non-firing brick using hydrothermal method, Journal of Science and
Technology 52 (4A) (2014) 198-204.
7. Pham Trung Kien, Do Minh Hien, Nguyen Hoc Thang, Pham Thi Lan Thanh. -
Innovation to recycle SiO2-sourced solid waste in glass and rice ash industry and
society, The 8th Regional Conference on Chemical Engineering in conjunction with
The 7th Vietnam National Chemical Congress and The 2nd Vietnam National
Chemical Engineering Congress, Ha Noi, Vietnam, 29 Nov – 01 Dec 2015, 304-305.
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8. Pham Trung Kien. - Ability to use wasted cullet in glass industry as environmental-
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section 1C-3, pp. 1.
TÓM TẮT
TỔNG HỢP KHOÁNG CALCIUM SILICATE HYDRATE (CSH)
TỪ NGUỒN NGUYÊN LIỆU TRẤU
Pham Trung Kien1*, Phan Viet Hoang1, Huynh Dai Phu1, Nguyen Van Tam2,
Ngo Vo Ke Thanh2, Nguyen Hoc Thang3, Hirofumi Hinode4
1Đại học Bách Khoa TP.HCM,
2Trung tâm Nghiên cứu triển khai - Khu Công nghệ cao TP.HCM,
3Đại học Công nghiệp Thực phẩm TP.HCM,
4Viện Công nghệ Tokyo.
*Email: phamtrungkien@hcmut.edu.vn
Việt Nam là nước nông nghiệp, sản xuất nhiều gạo và sản phẩm phụ là trấu. Trấu được
xem là chất thải nông nghiệp và được đốt bỏ. Quá trình này gây ô nhiễm môi trường, thu hút
nhiều nghiên cứu để tận dụng trấu. Nhóm nghiên cứu ở bộ môn Ceramic tận dụng trấu như
nguồn cung cấp silica (SiO2). Cần nhấn mạnh rằng thành phần chính của trấu là silica.
Nghiên cứu này công bố kỹ thuật mới phối trộn tro và CaO với tỷ lệ mol Ca/Si 1.0 để tổng
hợp khoáng xonotlite như vật liệu môi trường. Ưu điểm của nghiên cứu này là tận dụng
nguồn trấu Việt Nam và giảm tác hại lên môi trường bằng phản ứng thủy nhiệt.
Từ khóa: Calcium silicate, trấu, thủy nhiệt, ceramic.
Các file đính kèm theo tài liệu này:
- so_12_67_72_1407_2070818.pdf