| Literature DB >> 26935042 |
Veronika Pedrini-Martha1, Michael Niederwanger1, Renate Kopp1, Raimund Schnegg1, Reinhard Dallinger1.
Abstract
The terrestrial Roman snail Helix pomatia has successfully adapted to strongly fluctuating conditions in its natural soil habitat. Part of the snail's stress defense strategy is its ability to express Metallothioneins (MTs). These are multifunctional, cysteine-rich proteins that bind and inactivate transition metal ions (Cd(2+), Zn(2+), Cu(+)) with high affinity. In Helix pomatia a Cadmium (Cd)-selective, inducible Metallothionein Isoform (CdMT) is mainly involved in detoxification of this harmful metal. In addition, the snail CdMT has been shown to also respond to certain physiological stressors. The aim of the present study was to investigate the physiological and diurnal variability of CdMT gene expression in snails exposed to Cd and non-metallic stressors such as desiccation and oxygen depletion. CdMT gene expression was upregulated by Cd exposure and desiccation, whereas no significant impact on the expression of CdMT was measured due to oxygen depletion. Overall, Cd was clearly more effective as an inducer of the CdMT gene expression compared to the applied non-metallic stressors. In unexposed snails, diurnal rhythmicity of CdMT gene expression was observed with higher mRNA concentrations at night compared to daytime. This rhythmicity was severely disrupted in Cd-exposed snails which exhibited highest CdMT gene transcription rates in the morning. Apart from diurnal rhythmicity, feeding activity also had a strong impact on CdMT gene expression. Although underlying mechanisms are not completely understood, it is clear that factors increasing MT expression variability have to be considered when using MT mRNA quantification as a biomarker for environmental stressors.Entities:
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Year: 2016 PMID: 26935042 PMCID: PMC4774997 DOI: 10.1371/journal.pone.0150442
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
mRNA quantification and midgut gland Cd concentrations of controls and Cd exposed snails under consideration of differential feeding behavior.
| 30 | 296 180.99 (± 90 965.57) | 145 614.38–512 802.24 | 29 | 15.20 (± 8.09) | 6.22–36.08 | |
| Controls F | 18 | 310 982.40 (± 102 016.50) | 145 614.38–512 802.24 | 18 | 16.40 (± 9.04) | 7.65–36.08 |
| Controls NF | 12 | 273 978.87 (± 69 533.12) | 161 455.12–379 541.18 | 11 | 13.24 (± 6.15) | 6.22–28.45 |
| 30 | 856 605.90 (± 462 296.96) | 150 892.53–2 119 320.07 | 25 | 232.80 (± 144.13) | 24.12–455.98 | |
| Cd exp. F | 24 | 997 581.65 (± 402 865.71) | 513 301.29–2 119 320.07 | 20 | 274.28 (± 130.33) | 24.12–455.98 |
| Cd exp. NF | 6 | 292 702.89 (± 126 505.53) | 150 892.53–524 300.22 | 5 | 66.87 (± 30.67) | 36.97–110.82 |
Mean values, standard deviations (± SD) and range (from the lowest to the highest values) of mRNA copy numbers and Cd concentrations in μg/g d.w. of all control and Cd-exposed individuals (n = 30 each) are reported. Individuals of both groups are separated into feeders (F) and non-feeders (NF), and the respective copy numbers and Cd tissue concentrations are shown. Due to loss of samples during tissue digestion for metal analysis, numbers of snails listed for Cd concentrations can differ from those of mRNA quantification.