Influence of Wastewater Discharge on the Occurrence of PBTC, HEDP, and Aminophosphonates in Sediment, Suspended Matter, and the Aqueous Phase of Rivers

Sediment, suspended matter (SM), and water of a large river (Neckar; River1) and a small river (Körsch; River2) were analyzed for the phosphonates 2-phosphonobutane-1,2,4-tricarboxylic acid (PBTC), 1-hydroxyethylidene (1,1-diphosphonic acid) (HEDP), aminotris (methylphosphonic acid) (ATMP),...

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Main Authors: Eduard Rott, Oliver Happel, Dominic Armbruster, Ralf Minke
Format: Article
Language:English
Published: MDPI AG 2020-03-01
Series:Water
Subjects:
Online Access:https://www.mdpi.com/2073-4441/12/3/803
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spelling doaj-3ca243369abe40af8c7f4dd2fd2b26a62020-11-25T02:08:44ZengMDPI AGWater2073-44412020-03-0112380310.3390/w12030803w12030803Influence of Wastewater Discharge on the Occurrence of PBTC, HEDP, and Aminophosphonates in Sediment, Suspended Matter, and the Aqueous Phase of RiversEduard Rott0Oliver Happel1Dominic Armbruster2Ralf Minke3Institute for Sanitary Engineering, Water Quality and Solid Waste Management, University of Stuttgart, Bandtäle 2, 70569 Stuttgart, GermanyTZW: DVGW Water Technology Center, Karlsruher Straße 84, 76139 Karlsruhe, GermanyTZW: DVGW Water Technology Center, Karlsruher Straße 84, 76139 Karlsruhe, GermanyInstitute for Sanitary Engineering, Water Quality and Solid Waste Management, University of Stuttgart, Bandtäle 2, 70569 Stuttgart, GermanySediment, suspended matter (SM), and water of a large river (Neckar; River1) and a small river (K&#246;rsch; River2) were analyzed for the phosphonates 2-phosphonobutane-1,2,4-tricarboxylic acid (PBTC), 1-hydroxyethylidene (1,1-diphosphonic acid) (HEDP), aminotris (methylphosphonic acid) (ATMP), ethylenediaminetetra (methylene phosphonic acid) (EDTMP), and diethylenetriaminepenta (methylene phosphonic acid) (DTPMP). Ten samplings were performed at intervals of one to two months during one year, each covering the relevant matrices before and behind the discharge point of a wastewater treatment plant (WWTP). In River1, the total concentration of dissolved phosphonate did not change significantly (2.4&#8722;5.8 &#181;g/L before vs. 2.5&#8722;6.6 &#181;g/L behind WWTP; <i>p</i> = 0.9360). In River2, it increased significantly from &lt;0.1&#8722;1.6 &#181;g/L to 19&#8722;39 &#181;g/L (<i>p</i> &lt; 0.0001). Based on the median, the total phosphonate load in River1 sediment increased 1.9-fold (6.7&#8722;29.4 mg/kg before vs. 17.8&#8722;53.5 mg/kg behind WWTP; <i>p</i> = 0.0033) and in River2 by a factor of eight (1.8&#8722;5.0 mg/kg before vs. 18.1&#8722;51.4 mg/kg behind WWTP; <i>p</i> &lt; 0.0001). This indicates that phosphonates discharged by WWTPs adsorb onto solid particles and accumulate in the sediment. In the case of River2, the SM load could reach values of 1000&#8722;1710 mg/kg behind the WWTP, presumably due to the introduction of insufficiently retained activated sludge particles of &gt;2000 mg/kg phosphonate loads. In general, the nitrogen-free phosphonates PBTC and HEDP were most predominant in both dissolved and adsorbed form, of which HEDP had the highest adsorption affinity.https://www.mdpi.com/2073-4441/12/3/803atmpburdendepth profiledtpmpedtmpenvironmentpollutionriver concentration
collection DOAJ
language English
format Article
sources DOAJ
author Eduard Rott
Oliver Happel
Dominic Armbruster
Ralf Minke
spellingShingle Eduard Rott
Oliver Happel
Dominic Armbruster
Ralf Minke
Influence of Wastewater Discharge on the Occurrence of PBTC, HEDP, and Aminophosphonates in Sediment, Suspended Matter, and the Aqueous Phase of Rivers
Water
atmp
burden
depth profile
dtpmp
edtmp
environment
pollution
river concentration
author_facet Eduard Rott
Oliver Happel
Dominic Armbruster
Ralf Minke
author_sort Eduard Rott
title Influence of Wastewater Discharge on the Occurrence of PBTC, HEDP, and Aminophosphonates in Sediment, Suspended Matter, and the Aqueous Phase of Rivers
title_short Influence of Wastewater Discharge on the Occurrence of PBTC, HEDP, and Aminophosphonates in Sediment, Suspended Matter, and the Aqueous Phase of Rivers
title_full Influence of Wastewater Discharge on the Occurrence of PBTC, HEDP, and Aminophosphonates in Sediment, Suspended Matter, and the Aqueous Phase of Rivers
title_fullStr Influence of Wastewater Discharge on the Occurrence of PBTC, HEDP, and Aminophosphonates in Sediment, Suspended Matter, and the Aqueous Phase of Rivers
title_full_unstemmed Influence of Wastewater Discharge on the Occurrence of PBTC, HEDP, and Aminophosphonates in Sediment, Suspended Matter, and the Aqueous Phase of Rivers
title_sort influence of wastewater discharge on the occurrence of pbtc, hedp, and aminophosphonates in sediment, suspended matter, and the aqueous phase of rivers
publisher MDPI AG
series Water
issn 2073-4441
publishDate 2020-03-01
description Sediment, suspended matter (SM), and water of a large river (Neckar; River1) and a small river (K&#246;rsch; River2) were analyzed for the phosphonates 2-phosphonobutane-1,2,4-tricarboxylic acid (PBTC), 1-hydroxyethylidene (1,1-diphosphonic acid) (HEDP), aminotris (methylphosphonic acid) (ATMP), ethylenediaminetetra (methylene phosphonic acid) (EDTMP), and diethylenetriaminepenta (methylene phosphonic acid) (DTPMP). Ten samplings were performed at intervals of one to two months during one year, each covering the relevant matrices before and behind the discharge point of a wastewater treatment plant (WWTP). In River1, the total concentration of dissolved phosphonate did not change significantly (2.4&#8722;5.8 &#181;g/L before vs. 2.5&#8722;6.6 &#181;g/L behind WWTP; <i>p</i> = 0.9360). In River2, it increased significantly from &lt;0.1&#8722;1.6 &#181;g/L to 19&#8722;39 &#181;g/L (<i>p</i> &lt; 0.0001). Based on the median, the total phosphonate load in River1 sediment increased 1.9-fold (6.7&#8722;29.4 mg/kg before vs. 17.8&#8722;53.5 mg/kg behind WWTP; <i>p</i> = 0.0033) and in River2 by a factor of eight (1.8&#8722;5.0 mg/kg before vs. 18.1&#8722;51.4 mg/kg behind WWTP; <i>p</i> &lt; 0.0001). This indicates that phosphonates discharged by WWTPs adsorb onto solid particles and accumulate in the sediment. In the case of River2, the SM load could reach values of 1000&#8722;1710 mg/kg behind the WWTP, presumably due to the introduction of insufficiently retained activated sludge particles of &gt;2000 mg/kg phosphonate loads. In general, the nitrogen-free phosphonates PBTC and HEDP were most predominant in both dissolved and adsorbed form, of which HEDP had the highest adsorption affinity.
topic atmp
burden
depth profile
dtpmp
edtmp
environment
pollution
river concentration
url https://www.mdpi.com/2073-4441/12/3/803
work_keys_str_mv AT eduardrott influenceofwastewaterdischargeontheoccurrenceofpbtchedpandaminophosphonatesinsedimentsuspendedmatterandtheaqueousphaseofrivers
AT oliverhappel influenceofwastewaterdischargeontheoccurrenceofpbtchedpandaminophosphonatesinsedimentsuspendedmatterandtheaqueousphaseofrivers
AT dominicarmbruster influenceofwastewaterdischargeontheoccurrenceofpbtchedpandaminophosphonatesinsedimentsuspendedmatterandtheaqueousphaseofrivers
AT ralfminke influenceofwastewaterdischargeontheoccurrenceofpbtchedpandaminophosphonatesinsedimentsuspendedmatterandtheaqueousphaseofrivers
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