Dioxin impacts on lipid metabolism of soil microbes: towards effective detection and bioassessment strategies
Sabrin Mahfouz , Ghaytha Mansour , Denis J. Murphy , Abdulsamie Hanano
Bioresources and Bioprocessing ›› 2020, Vol. 7 ›› Issue (1) : 59
Dioxin impacts on lipid metabolism of soil microbes: towards effective detection and bioassessment strategies
Dioxins are the most toxic known environmental pollutants and are mainly formed by human activities. Due to their structural stability, dioxins persist for extended periods and can be transported over long distances from their emission sources. Thus, dioxins can be accumulated to considerable levels in both human and animal food chains. Along with sediments, soils are considered the most important reservoirs of dioxins. Soil microorganisms are therefore highly exposed to dioxins, leading to a range of biological responses that can impact the diversity, genetics and functional of such microbial communities. Dioxins are very hydrophobic with a high affinity to lipidic macromolecules in exposed organisms, including microbes. This review summarizes the genetic, molecular and biochemical impacts of dioxins on the lipid metabolism of soil microbial communities and especially examines modifications in the composition and architecture of cell membranes. This will provide a useful scientific benchmark for future attempts at soil ecological risk assessment, as well as in identifying potential dioxin-specific-responsive lipid biomarkers. Finally, potential uses of lipid-sequestering microorganisms as a part of biotechnological approaches to the bio-management of environmental contamination with dioxins are discussed.
Dioxins / Soil microbes / Lipid metabolism / Biodetection / Bioremediation
| [1] |
|
| [2] |
Aguilar‐Uscanga B, François JM (2003) A study of the yeast cell wall composition and structure in response to growth conditions and mode of cultivation. Lett Appl Microbiolo 37:268–274. https://doi.org/10.1046/j.1472-765X.2003.01394.x |
| [3] |
|
| [4] |
|
| [5] |
|
| [6] |
|
| [7] |
|
| [8] |
|
| [9] |
|
| [10] |
|
| [11] |
|
| [12] |
|
| [13] |
|
| [14] |
|
| [15] |
|
| [16] |
|
| [17] |
|
| [18] |
|
| [19] |
|
| [20] |
|
| [21] |
|
| [22] |
|
| [23] |
|
| [24] |
|
| [25] |
|
| [26] |
|
| [27] |
|
| [28] |
|
| [29] |
|
| [30] |
|
| [31] |
|
| [32] |
|
| [33] |
|
| [34] |
|
| [35] |
|
| [36] |
|
| [37] |
|
| [38] |
|
| [39] |
|
| [40] |
|
| [41] |
|
| [42] |
|
| [43] |
|
| [44] |
|
| [45] |
|
| [46] |
|
| [47] |
|
| [48] |
|
| [49] |
|
| [50] |
|
| [51] |
|
| [52] |
|
| [53] |
|
| [54] |
|
| [55] |
|
| [56] |
|
| [57] |
|
| [58] |
|
| [59] |
Fukui S, Tanaka A (1981) Metabolism of alkanes by yeasts, vol 19. In: Advances in biochemical engineering |
| [60] |
|
| [61] |
|
| [62] |
|
| [63] |
|
| [64] |
|
| [65] |
|
| [66] |
|
| [67] |
|
| [68] |
|
| [69] |
|
| [70] |
|
| [71] |
|
| [72] |
|
| [73] |
|
| [74] |
|
| [75] |
|
| [76] |
|
| [77] |
|
| [78] |
|
| [79] |
|
| [80] |
|
| [81] |
|
| [82] |
|
| [83] |
|
| [84] |
|
| [85] |
|
| [86] |
|
| [87] |
|
| [88] |
|
| [89] |
|
| [90] |
|
| [91] |
|
| [92] |
|
| [93] |
|
| [94] |
|
| [95] |
|
| [96] |
|
| [97] |
|
| [98] |
|
| [99] |
IPCS (2003) Polychlorinated biphenyls: human health aspects. Geneva: World Health Organization, International Programme on Chemical Safety (Concise International Chemical Assessment Document 55. https://www.inchem.org/documents/cicads/cicads/cicad55.htm) |
| [100] |
ISO/FDIS (2008) Soil quality—requirements and guidance for the selection and application of methods for the assessment of bioavailability of contaminants in soil and soil materials. https://www.isoorg/committee/54408.html |
| [101] |
|
| [102] |
|
| [103] |
|
| [104] |
|
| [105] |
|
| [106] |
|
| [107] |
|
| [108] |
|
| [109] |
|
| [110] |
|
| [111] |
|
| [112] |
|
| [113] |
|
| [114] |
|
| [115] |
|
| [116] |
|
| [117] |
|
| [118] |
|
| [119] |
|
| [120] |
|
| [121] |
|
| [122] |
|
| [123] |
|
| [124] |
|
| [125] |
|
| [126] |
|
| [127] |
|
| [128] |
|
| [129] |
|
| [130] |
|
| [131] |
|
| [132] |
|
| [133] |
|
| [134] |
|
| [135] |
|
| [136] |
|
| [137] |
|
| [138] |
|
| [139] |
|
| [140] |
|
| [141] |
|
| [142] |
|
| [143] |
|
| [144] |
NIEHS U (2017) Dioxins. National Institute of Environmental Health Sciences. https://www.niehs.nih.gov/health/topics/agents/dioxins/index.cfm |
| [145] |
|
| [146] |
|
| [147] |
|
| [148] |
|
| [149] |
|
| [150] |
|
| [151] |
|
| [152] |
|
| [153] |
|
| [154] |
|
| [155] |
|
| [156] |
|
| [157] |
|
| [158] |
|
| [159] |
|
| [160] |
|
| [161] |
|
| [162] |
|
| [163] |
|
| [164] |
|
| [165] |
|
| [166] |
|
| [167] |
|
| [168] |
|
| [169] |
|
| [170] |
|
| [171] |
|
| [172] |
|
| [173] |
|
| [174] |
|
| [175] |
|
| [176] |
|
| [177] |
|
| [178] |
|
| [179] |
|
| [180] |
|
| [181] |
|
| [182] |
|
| [183] |
|
| [184] |
|
| [185] |
|
| [186] |
|
| [187] |
|
| [188] |
|
| [189] |
|
| [190] |
|
| [191] |
Stockholm C (2001) Stockholm convention on persistent organic pollutants (POPs). Geneva, Secretariat of the Stockholm Convention. https://chm.pops.int |
| [192] |
|
| [193] |
|
| [194] |
|
| [195] |
|
| [196] |
|
| [197] |
|
| [198] |
|
| [199] |
|
| [200] |
|
| [201] |
|
| [202] |
|
| [203] |
|
| [204] |
|
| [205] |
|
| [206] |
|
| [207] |
|
| [208] |
|
| [209] |
|
| [210] |
|
| [211] |
WHO (2002) Polychlorinated dibenzodioxins, polychlorinated dibenzofurans, and coplanar polychlorinated biphenyls. In: Safety evaluation of certain food additives and contaminants. Geneva, World Health Organization (WHO Food Additives Series, No 48. https://www.inchem.org/documents/jecfa/jecmono/v48je20.htm) |
| [212] |
WHO (2016) World Health Organization fact sheet No 225, dioxins and their effects on human health, June 1999. https://www.who.int/mediacentre/factsheets/fs225/en/ |
| [213] |
|
| [214] |
|
| [215] |
|
| [216] |
|
| [217] |
|
| [218] |
|
| [219] |
|
| [220] |
|
| [221] |
|
| [222] |
|
| [223] |
|
| [224] |
|
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