scholarly journals Is the water disinfection by-product dichloroacetic acid biosynthesized in the edible mushroom Russula nigricans?

Chemosphere ◽  
2021 ◽  
pp. 130819
Author(s):  
Bassam Lajin ◽  
Simone Braeuer ◽  
Jan Borovička ◽  
Walter Goessler
2014 ◽  
Vol 13 (1) ◽  
pp. 54-66 ◽  
Author(s):  
Elisabet Teixidó ◽  
Esther Piqué ◽  
Javier Gonzalez-Linares ◽  
Joan M. Llobet ◽  
Jesús Gómez-Catalán

Disinfection by-products are contaminants produced during drinking water disinfection. Several DBPs have been implicated in a variety of toxic effects, mainly carcinogenic and genotoxic effects. Moreover, DBPs exposure has also been associated with an increased risk of developmental effects. In this study, the developmental toxicity and genotoxicity of 10 DBPs (four trihalomethanes [THMs], five haloacetic acids [HAAs] and sodium bromate) in the zebrafish embryo model were evaluated. Embryos exposed for 72 hours were observed for different endpoints such as growth, hatching success, malformations and lethality. THMs exposure resulted in adverse developmental effects and a significant reduced tail length. Two HAAs, tribromoacetic acid and dichloroacetic acid, along with sodium bromate were found to cause a significant increase in malformation rate. Chloroform, chlorodibromomethane and sodium bromate produced a weak induction of DNA damage to whole embryos. However, developmental effects occurred at a range of concentrations (20–100 μg/mL) several orders of magnitude above the levels that can be attained in fetal blood in humans exposed to chlorinated water. In conclusion, the teratogenic and genotoxic activity observed by some DBPs in zebrafish reinforce the view that there is a weak capacity of disinfection products to cause developmental effects at environmentally relevant concentrations.


2021 ◽  
Vol 1 (2) ◽  
pp. 11-14
Author(s):  
Rafat Moustafa ◽  
Ali M. Hassan ◽  
Hamdi A. Hammad ◽  
Ali M. Abdullah

Chlorine is the most common disinfectant used in drinking water treatment because it is cheap and has an efficient germicidal ability. However, chlorine and organic matter reacting trihalomethanes (THMs) are suspected carcinogens. The major groups of disinfection by-products (DBPs) are THMs, haloacetic acids (HAAs), haloacetonitriles (HANs), and halogenated ketones (HKs). Exposure to these by-products increases the risk of cancers, abortion, low birth weight, and congenital disabilities. The wastewater contents of organochlorine pesticides (OCPs), polychlorinated biphenyls (PCBs), as the source of total organic carbon (TOC) compounds, are oxidized by chlorine to produce DBPs. This study aimed to monitor the seasonal levels of THMs in Egypt compared with international standards using capillary gas chromatography. Results revealed that THMs mean values vary between 9.26 to 35.86 μg/l, while dichloroacetic acid (DCAA) and trichloroacetic acid (TCAA) mean values vary between 3.82 to 17.74 μg/l and 4.41 to 13.25 μg/l, respectively. The maximum THM and TCAA values were observed during the summer, probably due to high temperatures. While the maximum DCAA values were observed during the autumn due to the high levels of raw water TOC. In conclusion, continuous monitoring of THM and its species is highly recommended, taking into consideration how climate can influence THMs formation.


2018 ◽  
Vol 97 (2) ◽  
pp. 117-124 ◽  
Author(s):  
Margarita Yu. Vozhdaeva ◽  
A. R. Kholova ◽  
E. V. Vagner ◽  
E. A. Kantor ◽  
L. I. Kantor ◽  
...  

According to results of the estimation of drinking water on the index of the chemical harmlessness of five water intake structures of the city of Ufa, the drinking water of a superficial water intake on total and population cancerogenic risks was shown to be more harmful in comparison with water from infiltration water intakes. At the same time, drinking water from an infiltration water intake with ultra-violet disinfecting has smallest values of cancerogenic and non-cancerogenic risks. Trigalogenmetans and dichloroacetic acid (water disinfection chlorine by-products)| make the main contribution to the value of the total cancerogenic risk of the studied drinking waters, trigalogenmetans and di(2-ethylhexyl)phthalate make the contribution to the value of noncancerogenic risk. Polycyclic Aromatic Hydrocarbons fail to have a significant impact on the value of total cancerogenic risk of drinking water of the city in view of their presence at low concentration. Work is carried out according to R 2.1.10.1920-04 and MR 2.1.4.0032-11.


2017 ◽  
Vol 21 ◽  
pp. 174-178 ◽  
Author(s):  
Masahiko Isaka ◽  
Arunrat Yangchum ◽  
Sarunyou Wongkanoun ◽  
Surisa Kongthong

2018 ◽  
Vol 3 (1) ◽  
Author(s):  
Nusa Idaman Said

Water disinfection means the removal, deactivation or killing of pathogenic microorganisms. Microorganisms are destroyed or deactivated, resulting in termination of growth and reproduction. When microorganisms are not removed from drinking water, drinking water usage will cause people to fall ill. Chemical inactivation of microbiological contamination in natural or untreated water is usually one of the final steps to reduce pathogenic microorganisms in drinking water. Combinations of water purification steps (oxidation, coagulation, settling, disinfection, and filtration) cause (drinking) water to be safe after production. As an extra measure many countries apply a second disinfection step at the end of the water purification process, in order to protect the water from microbiological contamination in the water distribution system. Usually one uses a different kind of disinfectant from the one earlier in the process, during this disinfection process. The secondary disinfection makes sure that bacteria will not multiply in the water during distribution. This paper describes several technique of disinfection process for drinking water treatment. Disinfection can be attained by means of physical or chemical disinfectants. The agents also remove organic contaminants from water, which serve as nutrients or shelters for microorganisms. Disinfectants should not only kill microorganisms. Disinfectants must also have a residual effect, which means that they remain active in the water after disinfection. For chemical disinfection of water the following disinfectants can be used such as Chlorine (Cl2),  Hypo chlorite (OCl-), Chloramines, Chlorine dioxide (ClO2), Ozone (O3), Hydrogen peroxide etch. For physical disinfection of water the following disinfectants can be used is Ultraviolet light (UV). Every technique has its specific advantages and and disadvantages its own application area sucs as environmentally friendly, disinfection byproducts, effectivity, investment, operational costs etc. Kata Kunci : Disinfeksi, bakteria, virus, air minum, khlor, hip khlorit, khloramine, khlor dioksida, ozon, UV.


2020 ◽  
Vol 26 (1) ◽  
pp. 93-99
Author(s):  
Munekazu Kishimoto ◽  
Kazuo Nakamura ◽  
Takuto Tasaki ◽  
Kinya Matsumoto ◽  
Rina Nakano ◽  
...  

Sign in / Sign up

Export Citation Format

Share Document