| Literature DB >> 27366749 |
Katarzyna Godlewska1, Izabela Michalak1, Łukasz Tuhy1, Katarzyna Chojnacka1.
Abstract
We explored two methods for obtaining aqueous extracts: boiling and soaking of Baltic seaweeds (EB and ES, resp.). Algal extracts were characterized in terms of polyphenols, micro- and macroelements, lipids content, and antibacterial properties. The utilitarian properties were examined in the germination tests on Lepidium sativum for three extract dilutions (0.5, 2.5, and 10%). It was found that the extracts were similar in micro- and macroelement concentrations. Water was proved to be a good solvent to extract phenolic compounds. The algal extract produced by soaking biomass did not show inhibitory effect on Escherichia coli and Staphylococcus aureus. Only the boiled extract had an inhibitory activity against E. coli. Germination tests revealed a positive influence of the bioproducts on the cultivated plants. In the group treated with 10% EB, plants were 13% longer than in the control group; the content of elements B, Mo, Zn, and Na in the group treated with 10% ES was higher by 76%, 48%, 31%, and 59% than in the control group, respectively; the content of chlorophyll was 2.5 times higher in 0.5% ES than in the control group. Extracts showed the slight impact on the morphology of plants.Entities:
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Year: 2016 PMID: 27366749 PMCID: PMC4913069 DOI: 10.1155/2016/5973760
Source DB: PubMed Journal: Biomed Res Int Impact factor: 3.411
Multielemental composition of raw algal biomass and extracts obtained by boiling and soaking in water.
| Element | Baltic seaweeds (mg/kg d.m.) | EB | ES | Extract obtained by boiling (45 min, 60°C) | Extract obtained by boiling | Extract obtained by MAE 25°C | Extract obtained by MAE 40°C | Extract obtained by MAE 60°C |
|---|---|---|---|---|---|---|---|---|
| [ | [ | [ | ||||||
| mg/L | ||||||||
| Macroelements | ||||||||
| Ca | 40292 ± 8058 | 333 ± 50 | 410 ± 61 | 158 | — | 354 ± 53 | 363 ± 54 | 365 ± 54 |
| K | 5082 ± 1016 | 969 ± 145 | 978 ± 147 | 175 | 0.980 | 868 ± 130 | 901 ± 135 | 951 ± 142 |
| Mg | 3181 ± 636 | 300 ± 45 | 357 ± 54 | 108 | 9.28 | 303 ± 45 | 311 ± 46 | 322 ± 48 |
| Na | 6354 ± 1271 | 1239 ± 248 | 1302 ± 260 | 295 | 5.04 | 1050 ± 211 | 1200 ± 240 | 1250 ± 250 |
| P | 1155 ± 231 | 34.7 ± 5.2 | 5.22 ± 0.78 | — | — | 9.52 ± 1.43 | 18.3 ± 2.7 | 32.9 ± 4.9 |
| S | 8614 ± 1723 | 670 ± 100 | 599 ± 90 | — | — | 562 ± 84 | 582 ± 87 | 702 ± 105 |
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| Microelements | ||||||||
| B | 97.8 ± 14.7 | 6.50 ± 0.97 | 2.62 ± 0.39 | — | — | 3.30 ± 0.5 | 3.44 ± 0.51 | 4.74 ± 0.71 |
| Co | 2.84 ± 0.43 | 0.0100 ± 0.0025 | 0.0100 ± 0.0025 | — | 0.201 | 0.012 ± 0.003 | 0.012 ± 0.003 | 0.0135 ± 0.0034 |
| Cu | 12.7 ± 1.9 | 0.140 ± 0.021 | 0.0200 ± 0.005 | 1.15 | 3.02 | 0.117 ± 0.0117 | 0.148 ± 0.022 | 0.108 ± 0.016 |
| Fe | 6660 ± 1332 | 2.53 ± 0.38 | 17.6 ± 2.6 | 5.22 | 0.417 | 1.19 ± 0.2 | 2.17 ± 0.3 | 4.47 ± 0.70 |
| Mn | 232 ± 35 | 2.43 ± 0.36 | 3.71 ± 0.56 | — | 0.050 | 2.52 ± 0.37 | 2.62 ± 0.39 | 3.07 ± 0.46 |
| Mo | 0.310 ± 0.046 | 0.0200 ± 0.005 | 0.000 | — | — | 0.001 ± 0.000 | 0.179 ± 0.026 | 0.0108 ± 0.0027 |
| Ni | 5.23 ± 0.78 | 0.130 ± 0.019 | 0.120 ± 0.018 | — | — | 0.108 ± 0.016 | 0.111 ± 0.016 | 0.132 ± 0.019 |
| Si | 907 ± 136 | 9.10 ± 1.36 | 9.73 ± 1.46 | — | — | 3.10 ± 0.46 | 6.69 ± 1 | 11.9 ± 1.8 |
| Zn | 64.9 ± 9.7 | 0.240 ± 0.036 | 0.100 ± 0.015 | 1.25 | 1.02 | 0.0746 ± 0.0112 | 0.201 ± 0.03 | 0.169 ± 0.025 |
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| Toxic metals | ||||||||
| As | 3.90 ± 0.507 | 0.170 ± 0.022 | 0.160 ± 0.021 | — | — | 0.246 ± 0.032 | 0.150 ± 0.019 | 0.198 ± 0.025 |
| Cd | 0.710 ± 0.092 | <LLD | <LLD | — | — | <LLD | 0.001 ± 0.000 | 0.001 ± 0.000 |
| Pb | 7.03 ± 0.91 | 0.0400 ± 0.008 | 0.0100 ± 0.0025 | — | — | 0.0098 ± 0.002 | 0.0104 ± 0.0021 | 0.032 ± 0.006 |
The results of total height of the cultivated garden cress in the examined groups (N = 3).
| Group | Average height of cress (cm) ± SD |
|---|---|
| C | 5.36 ± 0.59a |
| EB 0.5% | 5.21 ± 0.59bcde |
| EB 2.5% | 5.10 ± 0.71fghi |
| EB 10% | 6.07 ± 0.61abf |
| ES 0.5% | 5.93 ± 0.75cg |
| ES 2.5% | 5.78 ± 0.93dh |
| ES 10% | 5.90 ± 0.86ei |
Three replicates for each group; 20 randomly selected plants in each replicate were measured.
a, b, c, d,…: statistically significant differences for p < 0.05.
The dry weight of garden cress in various experimental groups (N = 3).
| Group | Average dry weight of cress (g) ± SD |
|---|---|
| C | 0.0739 ± 0.0033 |
| EB 0.5% | 0.0727 ± 0.0037 |
| EB 2.5% | 0.0670 ± 0.0016 |
| EB 10% | 0.0733 ± 0.0033 |
| ES 0.5% | 0.0712 ± 0.0022 |
| ES 2.5% | 0.0680 ± 0.0010 |
| ES 10% | 0.0703 ± 0.0014 |
Three replicates for each group; all plants in each replicate were weighed.
Multielemental composition of the cultivated garden cress (mg/kg d.m., N = 3).
| Element | C | EB | ES | ||||
|---|---|---|---|---|---|---|---|
| 0.5% | 2.5% | 10% | 0.5% | 2.5% | 10% | ||
| Macroelements | |||||||
| Ca | 11161 ± 394 | 12752 ± 279 | 13126 ± 693 | 12956 ± 902 | 10818 ± 508 | 11881 ± 288 | 10475 ± 644 |
| K | 58067 ± 3802 | 65020 ± 291 | 67021 ± 1547 | 67774 ± 1430 | 68562 ± 190 | 67774 ± 2705 | 66983 ± 623 |
| Mg | 6974 ± 68 | 7188 ± 419 | 7210 ± 2 | 6854 ± 340 | 7662 ± 307 | 7409 ± 35 | 7456 ± 53 |
| Na | 1850 ± 8 | 1848 ± 181 | 2140 ± 24 | 3132.50 ± 92.79 | 2152.53 ± 97.27 | 2236.00 ± 170.10 | 2933.15 ± 51.10 |
| P | 16475 ± 964 | 16626 ± 798 | 16236 ± 301 | 14727 ± 686 | 16390 ± 170 | 17197 ± 211 | 16550 ± 83 |
| S | 15508 ± 939 | 15139 ± 488 | 14921 ± 166 | 12786 ± 999 | 15193 ± 260 | 17572 ± 1009 | 16155 ± 236 |
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| Microelements | |||||||
| B | 7.30 ± 0.82 | 11.3 ± 0.2 | 12.7 ± 0.52 | 12.7 ± 3.1 | 20.8 ± 13.0 | 15.1 ± 3.0 | 12.8 ± 0.9 |
| Co | 0.08 ± 0.03 | 0.11 | 0.09 ± 0.03 | 0.04 ± 0.01 | 0.12 ± 0.12 | 0.12 ± 0.05 | 0.21 ± 0.13 |
| Cu | 4.24 ± 0.07 | 5.75 ± 0.65 | 5.43 ± 0.85 | 4.72 ± 0.04 | 6.25 ± 1.21 | 9.80 ± 5.46 | 11.19 ± 2.49 |
| Fe | 278 ± 11 | 288 ± 46 | 279 ± 33 | 263 ± 13 | 198.79 ± 6.07 | 207 ± 3.0 | 227.77 ± 0.96 |
| Mn | 41.9 ± 1.85 | 47.6 ± 3.2 | 46.1 ± 1.6 | 45.0 ± 2.3 | 49.09 ± 0.13 | 49.04 ± 0.62 | 50.39 ± 1.00 |
| Mo | 1.20 ± 0.01 | 2.17 ± 0.47 | 1.73 ± 0.07 | 1.89 ± 0.14 | 1.79 ± 0.16 | 1.63 ± 0.14 | 1.77 ± 0.09 |
| Ni | 0.63 ± 0.16 | 1.44 ± 0.54 | 1.10 ± 0.02 | 0.84 ± 0.23 | 1.26 ± 0.13 | 1.23 ± 0.63 | 1.51 ± 0.13 |
| Si | 182 ± 22 | 271 ± 35 | 244 ± 38 | 226 ± 8.0 | 245 ± 71.49 | 192.25 ± 20.15 | 180.45 ± 8.41 |
| Zn | 58.22 ± 0.71 | 81.9 ± 2.7 | 88.2 ± 4.1 | 76.8 ± 0.2 | 88.6 ± 2.18 | 83.16 ± 0.04 | 76.35 ± 0.24 |
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| Toxic metals | |||||||
| As | 0.35 ± 0.12 | 0.17 ± 0.07 | 0.0521 ± 0.0104 | 0.36 ± 0.05 | 0.49 ± 0.59 | 0.15 ± 0.10 | <LLD |
| Cd | 0.26 ± 0.04 | 0.28 ± 0.01 | 0.24 ± 0.01 | 0.21 ± 0.01 | 0.31 ± 0.02 | 0.30 ± 0.02 | 0.24 ± 0.03 |
| Pb | 1.19 ± 0.01 | 1.52 ± 0.39 | 1.48 ± 0.05 | 1.53 ± 0.46 | 1.92 ± 0.62 | 1.44 ± 0.09 | 1.28 ± 0.01 |
Chlorophyll concentration in the cultivated garden cress (mg/L).
| Sample | Concentration of chlorophyll | Concentration of chlorophyll | Total chlorophyll concentration |
|---|---|---|---|
| C | 15.5 | 5.95 | 21.4 |
| EB 0.5% | 23.9 | 9.00 | 32.9 |
| EB 2.5% | 26.4 | 9.55 | 36.0 |
| EB 10% | 14.9 | 5.97 | 20.8 |
| ES 0.5% | 12.2 | 42.2 | 54.4 |
| ES 2.5% | 10.0 | 34.9 | 44.9 |
| ES 10% | 9.4 | 32.7 | 42.1 |
Figure 1The influence of algal extracts produced by boiling and soaking methods on plant morphology: (a) stalk, (b) leaf, internal part, and (c) leaf, external part of plant.