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Wastewater effluent

Effluent Wastewater or other liquid - raw (untreated), partially or completely... [Pg.612]

It is well documented that WWTP are major contributors of pharmaceuticals and illicit drugs in the aquatic environment, due to their incomplete removal in conventional activated sludge (CAS) treatment, resulting in important loads discharged into river waters through effluent wastewaters (Tables 1 and 2). [Pg.204]

Metal industries use substantial quantities of water in processes such as metal finishing and galvanized pipe manufacturing in order to produce corrosion-resistant products. Effluent wastewaters... [Pg.1191]

LOD-l,162 ng/L Spanish tap water Mean cone water from other countries Mean cone [Pg.32]

Influent wastewater Effluent wastewater River water... [Pg.194]

As it can be observed in Fig. 2, three out of the 16 investigated compounds, namely, heroin, lysergic acid diethylamide (LSD), and its metabolite 2-oxo, 3-hydroxy-LSD (O-H-LSD), were not detected in any wastewater sample. Two other target analytes, 6-acetyl morphine (6ACM) and A9-tetrahydrocannabinol (THC), were only present in influent wastewaters and with low detection frequencies. The most ubiquitous compounds, present in all influent and effluent wastewater samples analyzed, were the cocaine metabolite benzoylecgonine, and the amphetamine-like compounds ephedrine (EPH) and 3,4-methylenedioxymethamphetamine (MDMA or ecstasy). Cocaine, cocaethylene (CE, transesterification product of cocaine formed after the joint consumption of cocaine and ethanol), and morphine (MOR) were detected in all influent, but not in all effluent wastewaters (see Fig. 2). [Pg.194]

Fig. 3 Total levels of each investigated chemical class of illicit drugs and metabolites in the sampled wastewater (a) Influent wastewaters, (b) Effluent wastewaters... Fig. 3 Total levels of each investigated chemical class of illicit drugs and metabolites in the sampled wastewater (a) Influent wastewaters, (b) Effluent wastewaters...
Figure 4 shows the concentration range determined for each investigated drug and metabolite in the surface and wastewaters collected in the Ebro River basin, and its comparison with the drug levels found in similar studies carried out in other locations of Spain [6, 7,12,13,19, 31-33] and in various countries of the American [5, 10, 15, 22, 23] and the European continents [8, 9, 11, 14, 16-18, 21, 24-30]. Drug residue levels found in influent and effluent wastewaters from the Ebro River basin were mostly between the minimum and maximum concentrations described for these compounds in the peer-reviewed literature. Only, few compounds, e.g.,... [Pg.196]

Concentration range in influent wastewater 11 Concentration range in effluent wastewater s Concentration range in surface water... [Pg.196]

The fact that lower risks occur in areas with high river flow indicates that the dilution factor once pharmaceuticals enter river waters can efficiently mitigate possible environmental hazards, while in areas where effluent wastewaters represent a big percentage of the receiving river water flow hazards to aquatic organisms may increase. [Pg.232]

Ceglarek et al. [89] used the CW-TR fibre to analyse LAS in influent and effluent wastewater samples of a WWTP applying SPME. The optimised conditions included the addition of 0.5 g mL 1 of ammonium acetate to 3 mL of sample, extraction by immersion of the fibre (2 h) and static desorption (15 min) in isopropanol/methanol (1 1). The extracted LAS were analysed by SPME-HPLC-FD and LC-ESI-MS. The former was not suitable for quantifying LAS because of its limited extraction efficiency, whereas LC-ESI-MS showed a linear range from 0.5 to 100 xgL 1, with detection limits of 0.5 p.g L 1 for each individual homologue of LAS. The CW-TPR fibre also extracted alkylether sulfates (AESs) but not under optimised conditions. [Pg.438]

The eontrol of pH is a very important problem in maity processes, particularly in effluent wastewater treatment. The development and solution of mathematical models of these systems is, therefore, a vital part of chemical engineering dynamic modeling. [Pg.74]

Gomez MJ, Petrovic M, Femandez-Alba AR, Barcelo D (2006) Determination of pharmaceuticals of various therapeutic classes by solid-phase extraction and liquid chromatography-tandem mass spectrometry analysis in hospital effluent wastewaters. J Chromatogr A 1114 224-233... [Pg.167]

Plants with CR >70 percent are usually doing a good job of recovering condensate. CR values of <30 percent represent poor performance. Poor condensate recovery is expensive for two reasons. One reason is the energy and chemicals needed to prepare the boiler feedwater. But in recent years, there is a second, more expensive cost associated with poor condensate recovery effluent wastewater treatment. [Pg.175]

Although this chapter focuses on applications with effluent wastewaters, all types of aquatic environmental media (freshwater, brackish, marine) can be appraised with the pT-scale procedure. Testing of liquid samples is virtually unlimited and can include untreated and treated wastewater, surface water, ground water, porewater, elutriates and organic extracts of sediments. Applications could also be extended to assess toxicity of particle-bound substances in suspended matter and sediments. In this case, sample dilutions can be made with reference sediment material (Hoss and Krebs, 2003). The pT-method can also capture the effects of both soluble and particulate toxicity in a sample, provided that appropriate bioassays are employed. [Pg.123]

TABLE 5. Effluent—Wastewater Comparison (Flow Diagram/Figure 4, Reference Point 2). [Pg.2410]

ASBESTOS FIBER REMOVAL DURING EFFLUENT WASTEWATER TREATMENT. PILOT PLANT EVALUATION... [Pg.335]

Transport and fate of pollutants also depends upon the source of pollutants. Contaminants that originate from a definable source, for example, a smokestack or effluent (wastewater discharge) pipe, are known as point sources . Sometimes, however, the source of the pollutant is more diffuse for example, when pesticides are carried by runoff from a large area into a river. These sources are called nonpoint sources . Often, point and nonpoint sources may be combined or interconverted for example, if nonpoint runoff from a city is channeled into a discharge pipe via storm sewers. [Pg.1020]

A direct discharger is an industrial plant that discharges its effluent wastewater... [Pg.539]

Norwood DL, Michael LC, Cooper SD, et al. 1986. An application ofthe "Master Analytical Scheme" to influent and effluent wastewaters. In Advances in water analysis and treatment. Proceedings of Water Quality Technology Conference, Portland, OR, November, 365-386. [Pg.221]


See other pages where Wastewater effluent is mentioned: [Pg.239]    [Pg.218]    [Pg.32]    [Pg.33]    [Pg.33]    [Pg.78]    [Pg.212]    [Pg.213]    [Pg.219]    [Pg.219]    [Pg.220]    [Pg.224]    [Pg.225]    [Pg.225]    [Pg.229]    [Pg.70]    [Pg.72]    [Pg.166]    [Pg.299]    [Pg.74]    [Pg.446]    [Pg.19]    [Pg.4]    [Pg.116]    [Pg.116]    [Pg.542]    [Pg.294]    [Pg.378]   
See also in sourсe #XX -- [ Pg.236 ]




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