Abstract:Biosensors based on luminescent bacteria may be valuable tools to monitor the chemical quality and safety of surface and drinking water. In this review, an overview is presented of the recombinant strains available that harbour the bacterial luciferase genes luxCDABE, and which may be used in an online biosensor for water quality monitoring. Many bacterial strains have been described for the detection of a broad range of toxicity parameters, including DNA damage, protein damage, membrane damage, oxidative stre… Show more
“…The presence of sulfamethoxazole in the environment increases drug resistance of bacteria. There is a gradual increase in the number of bacteria strains that are resistant to sulfamethoxazole effects [103,104]. Tetracyclines show acute toxicity towards D. magna, D. rerioand C. auratus.…”
Rapid development of pharmaceutical industry, and thus widespread availability of different types of therapeutical and increased intake of pharmaceuticals, results in elevated concentrations of pharmaceuticals in municipal wastewater subjected to treatment in wastewater treatment plants. Pharmaceuticals present in raw wastewater discharged from hospitals, households, veterinary and health care clinics eventually end up in wastewater treatment plants. Commonly applied methods for treating wastewater do not allow complete removal of these contaminants. As a consequence, pharmaceuticals still present in treated wastewater are introduced to water environment. The most frequently identified pharmaceuticals in surface water belong to the following groups: non steroidal anti inflammatory drugs, beta-blockers, estrogens and lipid regulators. The most difficult is removal of diclofenac, clofibric acid and carbamazepine as these substances show low biodegradability. Diclofenac can be removed in the process of wastewater treatment by 40%, carbamazepine by 10%, and clofibric acid from 26 to 50%. The presence of diclofenac sodium in the rivers in Poland was confirmed and the concentrations were following: 380 ng/dm 3 (the Warta river), 470 ng/dm 3 (the Odra river), 140 ng/dm 3 (the Vistula river). Naproxene was found in the Warta river at the concentration of 100 ng/dm 3 . The presence of pharmaceuticals in surface water can be toxic to aqueous microorganisms and fish. Recent studies confirmed also the presence of pharmaceuticals in drinking water. This is considered as a problem especially in urban agglomerations such as Berlin or large cities in Spain and China. The studies showed that pharmaceuticals were also identified in the samples taken from the Polish rivers and drinking water. The presence of naproxene and diclofenac at the concentrations of 13 and 4 ng/dm 3 was identified in drinking water sampled from water intakes in Poznan. Surface water and drinking water showed also the presence of illegal drugs.
“…The presence of sulfamethoxazole in the environment increases drug resistance of bacteria. There is a gradual increase in the number of bacteria strains that are resistant to sulfamethoxazole effects [103,104]. Tetracyclines show acute toxicity towards D. magna, D. rerioand C. auratus.…”
Rapid development of pharmaceutical industry, and thus widespread availability of different types of therapeutical and increased intake of pharmaceuticals, results in elevated concentrations of pharmaceuticals in municipal wastewater subjected to treatment in wastewater treatment plants. Pharmaceuticals present in raw wastewater discharged from hospitals, households, veterinary and health care clinics eventually end up in wastewater treatment plants. Commonly applied methods for treating wastewater do not allow complete removal of these contaminants. As a consequence, pharmaceuticals still present in treated wastewater are introduced to water environment. The most frequently identified pharmaceuticals in surface water belong to the following groups: non steroidal anti inflammatory drugs, beta-blockers, estrogens and lipid regulators. The most difficult is removal of diclofenac, clofibric acid and carbamazepine as these substances show low biodegradability. Diclofenac can be removed in the process of wastewater treatment by 40%, carbamazepine by 10%, and clofibric acid from 26 to 50%. The presence of diclofenac sodium in the rivers in Poland was confirmed and the concentrations were following: 380 ng/dm 3 (the Warta river), 470 ng/dm 3 (the Odra river), 140 ng/dm 3 (the Vistula river). Naproxene was found in the Warta river at the concentration of 100 ng/dm 3 . The presence of pharmaceuticals in surface water can be toxic to aqueous microorganisms and fish. Recent studies confirmed also the presence of pharmaceuticals in drinking water. This is considered as a problem especially in urban agglomerations such as Berlin or large cities in Spain and China. The studies showed that pharmaceuticals were also identified in the samples taken from the Polish rivers and drinking water. The presence of naproxene and diclofenac at the concentrations of 13 and 4 ng/dm 3 was identified in drinking water sampled from water intakes in Poznan. Surface water and drinking water showed also the presence of illegal drugs.
“…Microbial biosensors are good tool for monitoring of chemical quality in surface and drinking water, and that are broadly reviewed [15,45]. The examples of environmental application of these devices are described in excellent work of Xu et al, 2013 [50].…”
Section: Genetically Engineered Bacteria In Genotoxicologymentioning
Abstract:The paper presents results of research concerning possibilities of applications of reporter-genes based microorganisms, including the selective presentation of defects and advantages of different new scientifi c achievements of methodical solutions in genetic system constructions of biosensing elements for environmental research. The most robust and popular genetic fusion and new trends in reporter genes technology -such as LacZ (β-galactosidase), xylE (catechol 2,3-dioxygenase), gfp (green fl uorescent proteins) and its mutated forms, lux (prokaryotic luciferase), luc (eukaryotic luciferase), phoA (alkaline phosphatase), gusA and gurA (β-glucuronidase), antibiotics and heavy metals resistance are described. Reporter-genes based biosensors with use of genetically modifi ed bacteria and yeast successfully work for genotoxicity, bioavailability and oxidative stress assessment for detection and monitoring of toxic compounds in drinking water and different environmental samples, surface water, soil, sediments.
“…Owing to the large number of enzymes and cofactors that the cells contain, a large variety of biosensors has been proposed for the detection of specific (groups of) analytes or for aquatic toxicity assessment, this latter application being addressed in section 2.3. Several reviews have been published on the topics (Lei et al, 2006), some of them being more specifically dedicated to yeast-based sensors (Baronian et al, 2004), geneticallymodified bacteria sensors (Daunert et al, 2000;Girotti et al, 2008;Hansen & Sorensen, 2001; Van der Meer & Belkin, 2010;Woutersen et al, 2010), or electrochemical cell biosensors ).…”
Section: Cell-based Biosensorsmentioning
confidence: 99%
“…Bacteria, yeasts, algae and fish cells have been also used for the development of toxicity biosensors (Baronian, 2004;Daunert et al, 2000;Hansen & Sorensen, 2001;Lei et al, 2006;Girotti et al, 2008;Van der Meer et al, 2010;Woutersen et al, 2010). The biosensor response may be due to a change in cell metabolism (inhibition of enzyme activity, respiration or photosynthesis), cell alteration, death, or change in the expression of certain genes (modified organisms).…”
Section: Biosensors Based On Whole Cellsmentioning
confidence: 99%
“…The most recent ones are given in Table 4. Optical biosensors are mainly based on luminescent modified bacteria, using typically the recA, uvrA, NrdA promoters for DNA damage detection, the grpE and dnaKp promoters for protein damage detection, and the fab A promoter for cell membrane damage (Woutersen et al, 2010).…”
Section: Biosensors Based On Whole Cellsmentioning
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