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Hydrothermal Conversion of Biomass Waste for Bio-based Chemicals

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Presentation on theme: "Hydrothermal Conversion of Biomass Waste for Bio-based Chemicals"— Presentation transcript:

1 Hydrothermal Conversion of Biomass Waste for Bio-based Chemicals
and Hydrochar Shicheng Zhang Shanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP3), Department of Environmental Science and Engineering, Fudan University, Shanghai

2 Content 1 Introduction 2 Hydrothermal liquefaction of biomass waste 3 Separation of liquefaction products for chemicals 4 Hydrochar and its application

3 1. Introduction Environmental problem & Resource recovery from biomass waste Water pollution (eutrophication) air pollution Enteromorpha Water hyacinth Biomass burning Algae Bloom in Lake Tai Ecological invasion

4 Components of Biomass Waste
Biomass waste is composed of cellulose, hemicellulose, lignin, lipids, proteins, pectin, organic acids, chlorophyll, polyphenols and so on.

5 Resource Recovery from Biomass Wastes @Fudan Bio-based Chemicals
Biooil Biofuels Hydrothermal liquefaction Green pesticide Waster Soluble Products Catalytic liquefaction Liquid Fertilizer BT 2014, 2015 ES&T 2014 Carbon 2014, 2016 Energ. Fuel. 2010, 2012, 2015 ACS Sus Chem Eng 2014, 2015 sand willow Porous Carbon Soil Amendment Water hyacinth Alternanthera philoxeroides Livestock manure Straw Solid Products hydrochar Biogas upgrading Enteromorpha Biogas Anaerobic Digestion Syngas biomethanation ES&T 2013, 2014 Water Res 2014 Biotechnol Bioeng 2012 BT 2016 Biotechnol Biofuel 2015, 2016 Hydrogen

6 2. Hydrothermal liquefaction of biomass waste
Hydrothermal liquefaction of macroalgae Enteromorpha Prolifera The maximum yield of bio-oil is 23.0 wt % obtained at 300℃, 30min, algae to water ratio of 1:7.5, with 5% Na2CO3, with HHVs around 30 MJ/kg. The bio-oil is a mixture of various compounds, and fatty acids are found the main compounds. Dong Zhou, Shicheng Zhang*, Jianmin Chen, et al. Energy & Fuels. 2010, 24, 4054–4061. (ESI paper)

7 2. Hydrothermal liquefaction of biomass waste
Liquefaction of macroalgae in alcohols methanol Ester compounds ethanol Low-Lipid Macroalgae Enteromorpha Prolifera White: methanol Gray: ethanol Dong Zhou, Shicheng Zhang*, Jianmin Chen, et al. Energy & Fuels. 2012, 26 (4),

8 2. Hydrothermal liquefaction of biomass waste
Catalytic liquefaction of rice straw to lactic acid NiO Rafia Younas, Shicheng Zhang*, Liwu Zhang*, et al. Catalysis Today. Accepted.

9 2. Hydrothermal liquefaction of biomass waste
Hydrothermal liquefaction of desert shrub Salix Psammophila The bio-oil is mainly composed of phenolic compounds. Changjun Li, Shicheng Zhang*, et al. BioResources. 2013, 8(2), Shicheng Zhang, et al. Chinese patent, ZL X; Chinese patent application number:

10 3. Products separation Two- stage nano-filtration and reverse osmosis
Monophenols separation Hang Lyu, Shicheng Zhang*, et al. Journal of Membrane Science. 2016, 504, 141.

11 3. Products separation Fine separation of bio-oil
Shicheng Zhang, et al. Chinese Patent Application number:

12 3. Products separation phenol Separation of phenolic compounds from the aqueous phase product Aqueous phase product 2-methoxy phenol phenol Modified Resin (DCX modified resin XAD4) 2-methoxy phenol The adsorption capacity of the modified resin was 1.5 times higher than that of the unmodified resin. other substances Kaifei Chen, Shicheng Zhang*, et al. Bioresource Technology 2015, 182,

13 N2 Porous carbon Hydrochar Properties Tetracycline adsorption
4. Hydrochar and its application Preparation of porous carbon by pyrolysis Hydrochar Porous carbon N2 Tetracycline adsorption Relationship Properties disadvantage:limited pore volume and adsorption ability, and hard collection Xiangdong Zhu, Shicheng Zhang*, et al. Carbon, 2014, 77,

14 4. Hydrochar and its application
Detailed results Porosity affected by activation temperature Adsorption performances Surface area and pore volume was increased after pyrolysis under N2. 500 ℃ is sufficient for activation of hydrochar. Adsorption capacity is closely related to porosity of porous carbon. However, the adsorption capacity is limited.

15 The link between hydrochar properties and porosity of activated carbon
decreases in surface area, pore volume strong correlations hydrochar-based activated carbon increases in stability, recalcitrance, aromaticity HTC peak temperature & retention time Activated carbon with high porosity is produced from low HTC temperature and time. Importantly, strong correlations between hydrochar properties and porosity of hydrochar based activated carbon was obtained. Xiangdong Zhu, Shicheng Zhang*, et al. ACS Sustainable Chem. Eng. 2015, 3, 833−840

16 Strong positive correlations
Detailed results Strong positive correlations Correlations between properties (mass loss, H/C, O/C) of hydrochar with surface area of activated carbon Xiangdong Zhu, Shicheng Zhang*, et al. ACS Sustainable Chem. Eng. 2015, 3, 833−840

17 4. Hydrochar and its application
Preparation of magnetic carbon composite by chemical co-precipitation advantage:high porosity and adsorption capacity disadvantage:weak acid resistance of magnetic particle There are big spaces to improve the porosity of magnetic composite Porosity of hydrochar, activated carbon and magnetic composite Xiangdong Zhu, Shicheng Zhang*, et al. ACS Sustainable Chemistry & Engineering, , (4),

18 4. Hydrochar and its application
Preparation of magnetic carbon composite by simultaneous activation and magnetization The as-prepared magnetic carbon composite have high porosity and high acid resistance. Xiangdong Zhu, Shicheng Zhang*, et al. Environmental Science & Technology, 2014; Bioresource Technology

19 The link between performances of magnetic carbon composite and hydrochar properties
strong correlations decreases in ID/IG acid resistance surface area & pore volume roxarsone adsorption HTC 160 200 240 270 300 Hydrochar increases in R50 index H/C, O/C, (O+N)/C Environmental performance of magnetic carbon composite is controlled by hydrochar properties. A magnetic carbon composite with strong acid resistance and low graphization degree is produced from low temperature hydrochar. Xiangdong Zhu, Shicheng Zhang*, et al. Energy & Fuels. 2015, Carbon 2016

20 Detailed results Correlations between R50 index
positive correlation negative correlation Correlations between R50 index of hydrochar with performances of magnetic carbon composite negative correlation

21 Detailed results Correlations between aromaticity
negative correlation positive correlation positive correlation Correlations between aromaticity (H/C atomic ratio) of hydrochar with performances of magnetic carbon composite

22 Summary Hydrothermal conversion of biomass waste for chemicals and materials is beneficial to the sustainable development of energy, resources and environment. The specific chemicals and carbon materials could be obtained by hydrothermal and catalytic conversion of biomass. Membrane separation and chromatography separation are efficent techniques for high purity chemicals. The properties of carbon materials could be easyly controlled by the properties of hydrochar and the activation conditions. In further researches and applications, it is essential to explore the directional conversion of biomass waste through catalytic methods or conbined technologies, as well as design continous process and scale-up for commercialization.

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