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The impact of persistent organic pollutants on freshwater ecosystems and human health

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Persistent organic pollutants general considerations. Modelling bioaccumulation circuits, POP scatering in the environment and adjacent risk assessment. GIS - in pollution modeling of persistent organic pollutants. The impact of persistent organic pollutants on human health. DDT - from a universal cure to an environmental problem. Persistent organic pollutants in continental aquatic ecosystems. The effects of DDT on physiological mechanisms in fish. Persistent organic pollutants in Mureș watershed.
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... The studied Mureș River is, regrettably, not excluded from this context; from this perspective, it is considered a European hotspot [29][30][31][32][33][34], having been impacted by humans from the Stone Age onwards [35][36][37][38][39]. It is the major tributary of the Tisza, situated between a longitude of 20°11′ E and 25°44′ E and a latitude of 45°14′ and 47°08′, with a length of 761 km and a basin surface area of 28,319 km 2 . ...
... The Mureș Basin was selected for this study for several reasons, including its large surface and rank within the Danube Basin [42], its large human population [40,43], and the related human activities and impact [29,33,34,[37][38][39]44] that disturb the river basin's ecological state. ...
... This river was chosen as it is the second longest river in Romania, after the Danube, and it traverses a significant portion of the country from east to west, passing some major cities including Târgu Mureș, Alba Iulia, Deva, Arad, etc. [33]. The samples were collected from 10 locations/cities with 3 sampling sites per location (on the river 200 m upstream of the WWTP effluent, on the river downstream of the WWTP effluent, and the WWTP effluent) and 3 extractions per sampling site, resulting in a total of 90 samples. ...
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The aim of this study was to assess the impact of WWTP effluents on the sediment microbial communities throughout the Mures , River. This study shows the existence of an ecological equilibrium between the WWTP effluent disruptors and the resilience of the Mures , River sediment microbiomes, a fact that suggests the river's stable/balanced ecological status in this regard, partly due to the microbial communities' resilience to the local impact of WWTP effluents. High-throughput 16S bacterial metabarcoding was used to evaluate the bacterial communities in the sediment. Due to the lotic system's sediment microbial communities' sensitivity to environmental changes, we assumed the dependency of these community structures and functions on environmental abiotic and abiotic parameters. The study results show that, although bacterial communities are equally diverse in the three locations (upstream WWTP, WWTP effluents, and downstream WWTP), there is a difference in community structure between the upstream samples and the WWTP samples, while the downstream samples contain a mixture of the upstream and WWTP effluent communities. Just downstream of the WWTP sediment, microbial communities are influenced by the specific input from the WWTP effluents; nevertheless, the river sediment microbiome is resilient and able to further recover its natural microbial composition, as evidenced by the similarity in bacterial community structures at all upstream river locations. This study demonstrates the ecological equilibrium between the WWTP effluent disruptors and the resilience capacity of the Mures , River sediment microbiomes, a fact that indicates the river's stable/balanced ecological status, in part due to the microbial communities' resilience to the local impact of WWTP effluents. Based on these findings, a monitoring system should be implemented here in the future.
... The second class includes the anthropogenically produced POPs, further subcategorized into eight classes (Table 1), according to their origin and parent structures as described in Fig. 1A (Akhtar et al., 2021). The second classification classifies POPs into three classes based on their function or human utilization (Curtean-Bȃnȃduc, 2016). The three classes are pesticides, chemicals used in industry, and by-products of industrial production (Fig. 1B). ...
Article
With the advent of the industrial revolution, the accumulation of persistent organic pollutants (POPs) in the environment has become ubiquitous. POPs are halogen-containing organic molecules that accumulate, and remain in the environment for a long time, thus causing toxic effects in living organisms. POPs exhibit a high affinity towards biological macromolecules such as nucleic acids, proteins and lipids, causing genotoxicity and impairment of homeostasis in living organisms. Proteins are essential members of the biological assembly, as they stipulate all necessary processes for the survival of an organism. Owing to their stereochemical features, POPs and their metabolites form energetically favourable complexes with proteins, as supported by biological and dose-dependent toxicological studies. Although individual studies have reported the biological aspects of protein-POP interactions, no comprehensive study summarizing the structural mechanisms, thermodynamics and kinetics of protein-POP complexes is available. The current review identifies and classifies protein-POP interaction according to the structural and functional basis of proteins into five major protein targets, including digestive and other enzymes, serum proteins, transcription factors, transporters, and G-protein coupled receptors. Further, analysis detailing the molecular interactions and structural mechanism evidenced that H-bonds, van der Waals, and hydrophobic interactions essentially mediate the formation of protein-POP complexes. Moreover, interaction of POPs alters the protein conformation through kinetic and thermodynamic processes like competitive inhibition and allostery to modulate the cellular signalling processes, resulting in various pathological conditions such as cancers and inflammations. In summary, the review provides a comprehensive insight into the critical structural/molecular aspects of protein-POP interactions.
... The Mureş River watershed was chosen for this research for various reasons: among them, its relatively large area and significance within the Danube Basin [47], the relatively large and important human population existing in this area, including major urban areas [45,46,48], the resulting human impacts and related problems in this basin [49][50][51][52][53][54][55][56]. These factors affect the diversity and the variability of environments over space and time and biocoenosis in the river and its watershed. ...
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Numerous sections of the Mureş River vary in terms of the abundance of nitrates, ammonia, and orthophosphates; and of correlated lotic sediment bacterial microbiome structures in terms of both diversity and abundance. This highlights the great versatility of microbiomes in being influenced by the physical-chemical characteristics of environments and their spatial changes. Bacteria microbiomes exhibit dynamic and shifting potential and significant tendencies toward self-organization and self-adaptation. These typical features represent an essential ecologic basis for lotic systems having to do with the use and reuse of various kinds of environmental resource as chemical substances. In this respect, trophic processes assure the river ecosystem optimum health ecologic status dynamic and trend, to be reached. The flexibility of shifting bacterial microbiomes is crucial in maintaining this ecological context’s vital role in biogeochemically sustaining other taxonomic groups, which are spatially and temporally continuous. This is especially important for nutrient cycle processes, even for rivers with high levels of negative human impact, in promoting a functional lotic system.
... The Mureş River basin contains over seven million people and accumulates the majority of the human communities' pollutants [11,12]. The origins here of potential POPs pollution are the chemical industry, intensive livestock farms, waste warehouses, water treatment plants, metallurgical factories, electrical transformer plant facilities, etc. [70]. Sediment, Ephemeroptera, and Trichoptera samples were collected on 7-16 August 2016 from the following sampling sites: M1, M2, M3, M4, M6, M7, M11, M12, and M14 on the Mureș River ( Figure 1). ...
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Persistent organic pollutants (POPs) have been at the forefront of environmental contamination research even before their ban in 2001 at the Stockholm Convention. Their relation to different compartments of the environment (biotic and abiotic) has been thoroughly investigated. This article aims to identify whether the benthos could represent a reliable indicator of environmental contamination with POPs and to highlight its potential transfer role between abiotic and upper trophic compartments-benthos feeders. In this regard, we determined that the Ephemer-optera samples have higher concentrations (p < 0.05) of ΣPCB, ΣHCH, and ΣDDT than sediment samples while Trichoptera samples have higher concentrations (p < 0.05) only in the case of ΣPCB and ΣDDT. This, along with the fact that the frequency of detection for POPs is similar between the sample types (sediments, Trichoptera, and Ephemeroptera), makes the benthos samples valuable indicators of contamination with sediment samples working as complementary information about how recent the contamination is.
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