Disinfection by-products formation and acute toxicity variation of hospital wastewater under different disinfection processes

2020 ◽  
Vol 238 ◽  
pp. 116405 ◽  
Author(s):  
Yuchen Luo ◽  
Li Feng ◽  
Yongze Liu ◽  
Liqiu Zhang
2009 ◽  
Vol 29 (3) ◽  
pp. 242-247 ◽  
Author(s):  
Masanori Terasaki ◽  
Masakazu Makino ◽  
Norihisa Tatarazako
Keyword(s):  

Author(s):  
Roger C. Prince ◽  
Bryan M. Hedgpeth ◽  
Aaron D. Redman ◽  
Josh D. Butler

ABSTRACT The acute toxicity of dispersed oil is well understood, and oil dilutes to levels below those of acute concern within hours of dispersion whether oil is dispersed by waves or by lower energy turbulence in the presence of chemical dispersants. Once dispersed, the hydrocarbon components of the spilled oil are degraded promptly by the native microbes in seawater, typically with an apparent half-life of 7–30 days even under Arctic conditions. Nevertheless, concern has been raised that this biodegradation might increase the oil's acute toxicity by generating and releasing toxic by-products. We show here, using Americamysis bahia as the test species, that this does not occur when dispersed oil is present at environmentally-relevant concentrations (initially 3 ppm oil dispersed with Corexit 9500 at a dispersant to oil ratio of 1:20). The guidelines for this toxicity test mandate a temperature of 26 ± 1C, rather warmer than the temperature of collection of the seawater from the New Jersey shore that we used as our experimental medium, so it is not surprising that biodegradation was especially rapid with a half-life for the loss of detectable hydrocarbons of approximately 4 days. We conducted sequential 4-day acute toxicity tests for 20 days, by which time the indigenous microorganisms had removed almost 80% of the detectable hydrocarbons in the lightly weathered crude oil. We saw no mortality in any of the five sequential tests.


2001 ◽  
Vol 66 (2) ◽  
pp. 255-262 ◽  
Author(s):  
M. W. Toussaint ◽  
L. M. Brennan ◽  
A. B. Rosencrance ◽  
W. E. Dennis ◽  
F. J. Hoffmann ◽  
...  

2008 ◽  
Vol 58 (1) ◽  
pp. 259-265 ◽  
Author(s):  
C. Zaror ◽  
C. Segura ◽  
H. Mansilla ◽  
M. A. Mondaca ◽  
P. González

This paper presents experimental results on the effect of temperature on the rate of Imidacloprid removal from waste water using homogeneous photo-Fenton processes. Experiments were conducted in a 2 L photo reactor set at 15–42°C, initial concentrations in the range of 10 to 40 mg L−1 Fe(II) and 100–450 mg L−1 H2O2; 30 150 min processing times. Initial H2O2 concentration determined the extent of the oxidation process, whereas iron concentration played a key role in the process kinetics. Homogeneous photo-Fenton showed a fast initial reaction leading to 50% Imidacloprid degradation after less than 1 min of treatment, followed by a slower process until full removal was achieved. Rapid Fe(II) oxidation to Fe(III) seems responsible for the initial Imidacloprid removal. Imidacloprid removal fitted well a pseudo-first order kinetic scheme, with apparent activation energy of approximately 31.6 kJ/mole. Untreated Imidacloprid samples showed significant acute toxicity to Daphnia magna and genotoxic effects on Bacillus subtilis. Acute toxicity and genotoxicity remained detectable even after complete pesticide removal, showing that toxic by-products were present. The design and operation of photo Fenton processes should focus on toxicity removal rather than on specific target pollutants.


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