| Literature DB >> 35683284 |
Xun He1, Hui Jiang1, Xin Wan1, Kequan Chen1, Pingkai Ouyang1.
Abstract
The filter mud in molasses has a significant inhibitory effect on biological activity and cannot be utilised by organisms; therefore, before molasses are biotransformed, the filter mud will be separated and directly discarded in the environment. In this study, the filter mud was used as the retarder of cement concrete OPC 42.5 for the first time. It was found that when 0.2-0.8% filter mud was added to fresh cement concrete OPC PC 42.5, the hardening time of cement slurry was significantly prolonged due to the synergistic retarding effect of sugar, colloid and total cellulose in the filter mud. In addition, the compressive strength of cement concrete mixed with the filter mud in the early stage (<10 days), middle stage (10-100 days) and later stage (180 days) was significantly higher than that of cement concrete and cement concrete mixed with commercial asphalt lignosulfonate. These results showed that the filter mud in molasses could realise harmless and resource utilisation, which could promote the comprehensive utilisation of molasses.Entities:
Keywords: biochemical engineering; biomass; biorefinery; chemical processes; molasses; retardation effect
Year: 2022 PMID: 35683284 PMCID: PMC9181882 DOI: 10.3390/ma15113989
Source DB: PubMed Journal: Materials (Basel) ISSN: 1996-1944 Impact factor: 3.748
Properties and composition of cement.
| Physical Properties | Mechanical Properties |
|---|---|
| Density (g/m3) 3.15 | Compressive strength/MPa |
| Blaine sp. surface (cm2/g) 3900 | Chemical components/% |
| Grade | |
| Setting time (min) |
Figure 1Separation steps of molasses raw material.
The distribution of molasses components.
| Composition | Molasses Material/% | Filter Mud/% | Molasses Colloids/% | Sugar Liquid/% |
|---|---|---|---|---|
| Free sugar | 52.81 ± 0.02 | 3.98 ± 0.18 | -- a | 40.60 ± 2.45 |
| Colloids | 15.92 ± 1.25 | 2.25 ± 0.08 | 12.85 ± 1.14 | -- |
| Holocellulose | 3.22 ± 0.14 | 3.22 ± 0.58 | -- | -- |
| Ash | 5.05 ± 0.79 | 1.75 ± 0.67 | 1.36 ± 0.02 | 1.23 ± 0.11 |
a—indicated “no detection”.
Effects of different additives on cement condensation time.
| Admixture Ratio | 0% | 0.2% | 0.4% | 0.8% | ||||
|---|---|---|---|---|---|---|---|---|
| Start/min | End/min | Start/min | End/min | Start/min | End/min | Start/min | End/min | |
| Ca-lignosulfonate | 150 ± 10 | 265 ± 10 | 210 ± 8 | 311 ± 10 | 282 ± 5 | 363 ± 13 | 413 ± 12 | 538 ± 3 |
| Molasses material | 150 ± 10 | 265 ± 10 | 454 ± 11 | 558 ± 6 | 732 ± 13 | 985 ± 17 | 920 ± 11 | 1258 ± 12 |
| Water-soluble pigment | 150 ± 10 | 265 ± 10 | 150 ± 2 | 265 ± 12 | 153 ± 8 | 267 ± 9 | 155 ± 11 | 272 ± 9 |
| Sugars | 150 ± 10 | 265 ± 10 | 421 ± 12 | 500 ± 10 | 673 ± 2 | 863 ± 22 | 888 ± 21 | 1098 ± 28 |
| Sucrose | 150 ± 10 | 265 ± 10 | 423 ± 23 | 503 ± 2 | 688 ± 12 | 877 ± 12 | 900 ± 12 | 1197 ± 20 |
| Molasses colloids | 150 ± 10 | 265 ± 10 | 113 ± 17 | 228 ± 19 | 98 ± 10 | 189 ± 18 | 65 ± 11 | 132 ± 10 |
| Filter mud in molasses | 150 ± 10 | 265 ± 10 | 298 ± 11 | 416 ± 7 | 485 ± 12 | 738 ± 21 | 752 ± 14 | 1072 ± 16 |
Workability properties and air contents of fresh concretes.
| Admixture Content/% | Molasses Material | Filter Mud | Ca-Lignosulfonate |
|---|---|---|---|
| Fresh concrete/cm | |||
| 0.2 | 14.8 ± 0.2 | 15.7 ± 0.3 | 17.0 ± 0.3 |
| 0.4 | 18.7 ± 0.2 | 19.9 ± 0.4 | 21.8 ± 0.5 |
| Air contents/% | |||
| 0.2 | 0.5 ± 0.05 | 0.8 ± 0.03 | 1.4 ± 0.05 |
| 0.4 | 0.7 ± 0.02 | 1.0 ± 0.05 | 1.8 ± 0.03 |
Figure 2Effects of different additives on the total bleeding water of fresh cement.
Figure 3Effects of different additives on the cement compressive strength. (a) concrete with 0.2% retarder, (b) concrete with 0.4% retarder.
Sorptivities of concretes.
| Condition | Sorptivity (mm/min) | ||
|---|---|---|---|
| Molasses Material | Filter Mud | Ca-Lignosulfonate | |
| 28 d in water | 0.238 ± 0.15 | 0.221 ± 0.12 | 0.164 ± 0.08 |
Figure 4Monitoring drying shrinkage of concretes for admixture content of 0.4%.
Figure 5Variation of resonant frequency with freezing–thawing cycles.
The changes of ultrasound velocity and weight of concretes under freezing–thawing cycles.
| Admixture | ||||
|---|---|---|---|---|
| Molasses Material | Filter Mud | Ca-Lignosulfonate | ||
| Ultrasound velocity(km/s) | Initial | 4216 ± 20 | 4223 ± 12 | 4219 ± 15 |
| After 100 cycles | 3949 ± 15 | 3923 ± 21 | 3690 ± 7 | |
| Change/% | 6.33 ± 0.25 | 7.10 ± 1.33 | 12.54 ± 0.98 | |
| Weight of specimen/g | Initial | 12,230 ± 25 | 12,246 ± 23 | 12,126 ± 12 |
| After 100 cycles | 12,143 ± 11 | 12,146 ± 17 | 12,035 ± 24 | |
| Change/% | 0.71 ± 0.11 | 0.82 ± 0.13 | 0.75 ± 0.22 | |
Figure 6Variation of resonant frequency with wetting–drying cycles.
The changes of ultrasound velocity and weight of concretes under wetting–drying cycles.
| Admixture | ||||
|---|---|---|---|---|
| Molasses Material | Filter Mud | Ca-Lignosulfonate | ||
| Ultrasound velocity (km/s) | Initial | 4423 ± 14 | 4435 ± 21 | 4322 ± 32 |
| After 60 cycles | 3776 ± 12 | 3679 ± 35 | 3580 ± 23 | |
| Change/% | 14.63 ± 1.35 | 17.05 ± 2.11 | 17.17 ± 2.41 | |
| Weight of specimen/g | Initial | 12,318 ± 25 | 12,352 ± 23 | 12,245 ± 12 |
| After 60 cycles | 12,103 ± 25 | 12,188 ± 22 | 11,947 ± 14 | |
| Change/% | 1.75 ± 0.14 | 1.32 ± 0.24 | 2.43 ± 0.15 | |
Figure 7Effects of admixture on carbonation depth.