Reda Gado

Dr. Reda Gado

orcid

Research Focus & Metrics

Academic Career Length

13Years (2014-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 September 2016 in Process Safety and Environmental Protection
Verified
Journal Article
Closed access
MZMahmoud F. Zawrah
Mahmoud F. Zawrah
RGReda Gado
Reda Gado
NFN. Feltin
N. Feltin
SDS. Ducourtieux
S. Ducourtieux
LDL. Devoille
L. Devoille

1 June 2016 in Construction and Building Materials
Verified
Journal Article
Closed access
EEE.A. El-Alfi
E.A. El-Alfi
RGReda Gado
Reda Gado

14 January 2020 in Materials
Verified
Journal Article
Open access
PDF file
RGReda Gado
Reda Gado
MHMarek Hebda
Marek Hebda
Michał ŁachMichał Łach
Michał Łach
JMJanusz Mikuła
Janusz Mikuła
This study was conducted to investigate the influence of various reaction conditions, namely the silica modulus SiO2/Na2O, H2O/Na2O molar ratio, and liquid/solid ratio on the geopolymerization reaction of the waste fired clay bricks (Grog). The starting raw material and the generated geopolymer specimens produced by different geopolymerization reaction conditions have been characterized using different techniques: X-ray diffraction (XRD), Fourier-transform infrared spectroscopy (FTIR), scanning electron microscope (SEM) and thermal analysis. Furthermore, physico–mechanical characterization has been carried out through the determination of bulk density, porosity, water absorption, and compressive strength for each sample at interval curing times of up to 28 days. The results indicated that the geopolymerization system of the waste fired clay bricks is influenced by the investigated reaction conditions at room temperature. The compressive strength of the geopolymer sample produced at optimum conditions increased significantly by up to 37.5 MPa, in comparison with 4.5 MPa for other conditions. Finally, an optimum recommendation and useful conclusions concerning the recycling and utilization of this waste material through the geopolymerization process are made for compatibility with construction applications.

1 March 2014 in Spectrochimica Acta Part A: Molecular and Biomolecular Spectroscopy
Verified
Journal Article
Closed access
MZMahmoud F. Zawrah
Mahmoud F. Zawrah
RKR.M. Khattab
R.M. Khattab
ESE.M. Saad
E.M. Saad
RGReda Gado
Reda Gado

31 July 2018 in The Open Materials Science Journal
Verified
Journal Article
Open access
PDF file
MZMahmoud F. Zawrah
Mahmoud F. Zawrah
RGReda Gado
Reda Gado
RKR. M. Khattab
R. M. Khattab
Object: Geopolymers mixes were fabricated from Metakaolin (MK) and Blast Furnace Slag (BFS) waste material in the presence of sodium hydroxide and sodium silicate which were used as alkali activators. To optimize the suitable amount of slag, eleven batches were designed, mixed and homogenized for 30 min.Method: To determine the suitable amount of liquid required for pasting, normal consistency and setting time were determined. The physico-mechanical properties at different curing agesi.e. 3, 7, 28 and 90 days, were determined. X-ray diffraction and scanning electron microscope were used to investigate phase composition and microstructure.Result: To guarantee forming geopolymer gel and to check its amount, HCl extraction test was performed. Salicylic acid/methanol extraction was also performed to verify the presence and amount of Calcium Silicate Hydrate (CSH). The results revealed that calcium-rich slag (BFS) accelerated the hardening process and decreased the alkaline liquid consistency. For geopolymer without BFS, two phases, namely; un-reacted metakaolin and geopolymer gel were formed. For geopolymers with BFS, three phases were formed, namely; un-reacted metakaolin, geopolymer gel and CSH with aluminum substitution (CASH) gel. The bulk density was increased with increasing BFS and curing time. The strength was increased with increasing of BFS, reaching its maximum (about 120 MPa) for the specimen containing 70% slag, cured for 28 days.

18 February 2021 in Materials
Verified
Journal Article
Open access
PDF file
Michał ŁachMichał Łach
Michał Łach
RGReda Gado
Reda Gado
JMJoanna Marczyk
Joanna Marczyk
CZCelina Ziejewska
Celina Ziejewska
Neslihan Doğan-SağlamtimurNeslihan Doğan-Sağlamtimur
Neslihan Doğan-Sağlamtimur
MHMarek Hebda
Marek Hebda
Alkali activated cement (AAC) can be manufactured from industrial by-products to achieve goals of “zero-waste” production. We discuss in detail the AAC production process from (waste) post-production clay, which serves as the calcium-rich material. The effect of different parameters on the changes in properties of the final product, including morphology, phase formation, compressive strength, resistance to the high temperature, and long-term curing is presented. The drying and grinding of clay are required, even if both processes are energy-intensive; the reduction of particle size and the increase of specific surface area is crucial. Furthermore, calcination at 750 °C ensure approximately 20% higher compressive strength of final AAC in comparison to calcination performed at 700 °C. It resulted from the different ratio of phases: Calcite, mullite, quartz, gehlenite, and wollastonite in the final AAC. The type of activators (NaOH, NaOH:KOH mixtures, KOH) affected AAC mechanical properties, significantly. Sodium activators enabled obtaining higher values of strength. However, if KOH is required, the supplementation of initial materials with fly ash or metakaolin could improve the mechanical properties and durability of AAC, even c.a. 28%. The presented results confirm the possibility of recycling post-production clay from the Raciszyn II Jurassic limestone deposit.