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À̸§ °ü¸®ÀÚ waterindustry@hanmail.net ÀÛ¼ºÀÏ 2013.03.19 Á¶È¸¼ö 747
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Antwerp ´ëÇÐ Alexander van Nuijs ±³¼öÆÀ ¿¬±¸Á¶»ç
 

ÀÜ·ù ÀǾ๰Áú ¹× ¹ýÀûÀ¸·Î ±ÝÁöµÈ ¾à¹°Àº »ç¶÷ ¶Ç´Â µ¿¹°µé·ÎºÎÅÍ ¹è¼³µÇ¾î °­, ÇÏõ¼ö ¹× Çϼöó¸®Àå¿¡¼­ °ËÃâµÉ ¼ö ÀÖ´Ù. ÀÌ·¯ÇÑ ¹°ÁúµéÀº »ýÅÂ°è ±³¶õ ¹× ºÎÀûÀýÇÑ ÀǾàÇ°ÀÇ ³ëÃâ»Ó¸¸ ¾Æ´Ï¶ó ÇϼöÀÇ Áø¿øÁöÀÎ Áö¿ª»çȸ¿¡¼­ »ç¿ëµÇ°í ÀÖ´Â ¾à¹°»ç¿ë ½ÇŸ¦ ÆľÇÇϴµ¥ Å« µµ¿òÀÌ µÈ´Ù.
 
Çϼöó¸®Àå¿¡¼­´Â ¹°¸® È­ÇÐÀû 󸮰úÁ¤À» ÅëÇÏ¿© ÀüºÎ´Â ¾Æ´ÏÁö¸¸ ÀϺΠ¾à¹°µéÀÌ Á¦°ÅµÇ±â ¶§¹®¿¡ º¸´Ù Á¤È®ÇÏ°Ô ±× Áö¿ª¿¡ »ç¿ëµÇ´Â ¾à¹°»ç¿ë ½ÇŸ¦ ÃßÀû Á¶»çÇϱâ À§Çؼ­´Â Çϼöó¸®Àå À¯ÀÔ¼ö¿¡¼­ °Ëü¸¦ ÃëÇÏ´Â °ÍÀÌ ¹Ù¶÷Á÷ÇÏ´Ù.
 
Áö±Ý±îÁö ¿¬±¸Á¶»ç´Â ÀϹÝÀûÀ¸·Î Àß ¾Ë·ÁÁø ¸¶¾à·ù(ÄÚÄ«ÀÎ, ¸ð¸£ÇÉ, ¾ÏÆ䟹Î, Çì·ÎÀÎ, Çì·ÎÀÎ ´ë»ç¹°Áú)µé¿¡ ÁýÁߵǾú´Ù.
 
ÇÏÁö¸¸ ÃÖ±Ù º§±â¿¡ Antwerp ´ëÇÐÀÇ Alexander van Nuijs¿Í ±×ÀÇ µ¿·áµéÀº Çϼöó¸®ÀåÀÇ À¯ÀÔ¼ö¿¡¼­ ±âÁ¸ ¸¶¾à·ù ¿Ü¿¡ ½ÅÁ¾ ºÒ¹ý ¾à¹°·Î¼­ ÄÉŸ¹Î(Ketamine), ÄÉŸ¹Î ´ë»çüÀÎ ³ë¸£ÄÉŸ¹Î(norKetamine), ÄÉÄ¡³í ´ë»çüÀÎ ¸ÞÄ¥·»µð¿Á½ÃÇǷι߷¹·Ð (methylenedioxy pyrovalerone: MDPV), ¸ÞÆäµå·Ð(mephdrone, MEPH)°ú ´ë¸¶ À¯µµÃ¼ÀÎ THC-COOH¸¦ ¾×üũ·Î¸¶Åä±×·¡ÇÇ-ÅÙµ©Áú·®ºÐ¼®±â¸¦ »ç¿ëÇÏ¿© Ãß°¡ÀûÀ¸·Î ¿¬±¸Á¶»çÇÏ¿´´Ù. ½ÇÁ¦ ÀÚ¼¼ÇÑ ºÐ¼® ¹æ¹ý°ú °á°ú´Â ¡°Drug Testing and Analysis 2013¡± ¿¡ ¼Ò°³µÇ¾ú´Ù.
 
10¸¸¸íÀÌ ³Ñ°Ô °ÅÁÖÇÏ´Â º§±â¿¡ÀÇ Brussels°ú Antwerp ¹è¼öÁö¿ªÀÇ Çϼöó¸®Àå¿¡¼­ ¸î ÁÖ µ¿¾È 24½Ã°£ ³»³» À¯ÀÔ¼ö¸¦ äÃëÇÑ ÈÄ °Ëü·ÎºÎÅÍ Å¸±ê È­ÇÕ¹°µéÀ» °í»óÃßÃâ(solid-phase extraction)ÇÏ¿© ¿ª»óÄ÷³À» ÅëÇÏ¿© ºÐ¸®ÇÏ°í THC-COOH´Â Áú·®ºÐ¼®±âÀÇ À½ÀÌ¿Â ¸ðµå·Î °ËÃâÇÏ°í ³ª¸ÓÁö´Â ¾çÀÌ¿Â ¸ðµå·Î °ËÃâÇÏ¿´´Ù.
 
³ë¸£ÄÉŸ¹Î°ú µðÇÏÀ̵å·Î³ë¸£ÄÉŸ¹ÎÀÇ °ËÃâ ÇÇÅ©´Â ºÎºÐÀûÀ¸·Î ºÐ¸®µÇÁö ¸øÇÏÁö¸¸ »óÈ£ ´Ù¸¥ Á¶°¢ÀÌ¿Â(daughter ion)À» MRM(multiple reaction monitoring) ¸ðµå¿¡¼­ °¢ ¸ñÀû È­ÇÕ¹°°ú ´ë»çü¸¸ÀÇ Æ¯Á¤ »ý¼º À̿¸¸À» ¸ð´ÏÅ͸µÇÏ¿© °¢ °¢ÀÇÈ­ÇÕ¹°À» Á¤·®Çϴµ¥ ¹æÇصÇÁö ¾Ê¾Ò´Ù.
 
º§±â¿¡ Brussels°ú Antwerp ¹è¼öÁö¿ª ¿¬±¸Á¶»ç °á°ú, ½ÅÁ¾ ¸¶¾à·ùÀÎ THC-COOH¿Í ÄÉŸ¹ÎÀº ¸ðµç »ùÇÿ¡¼­ °ËÃâµÇ¾ú°í, ³ë¸£ÄÉŸ¹Î ¿ª½Ã °ËÃâµÇ¾úÀ¸³ª ³ë¸£ÄÉŸ¹ÎÀº °ËÃâÇÑ°è ÀÌÇÏ·Î °ËÃâµÇ¾î Á¤·®ÇÒ ¼ö´Â ¾ø¾ú´Ù. ±× ¿Ü ´Ù¸¥ ½ÅÁ¾ ¸¶¾à·ù´Â ¹ß°ßµÇÁö ¾Ê¾Ò´Ù.
 
À̹ø ¿¬±¸°á°ú´Â ½ºÆäÀΰú ¿µ±¹ÀÇ Çϼöó¸®Àå ¿¬±¸Á¶»ç °á°ú¿Í ºñ±³ÇÏ¿´À» ¶§ º§±â¿¡ Áö¿ª¿¡¼­ ÄÉŸ¹Î°ú THC-COOHÀÇ ¾à¹°»ç¿ë ½ÇÅ´ ¸íÈ®ÇÏ°Ô °üÂûµÇÁö ¸øÇÏ¿´À¸³ª ÄÉŸ¹ÎÀº ³·Àº ¼öÁØÀ¸·Î, THC-COOH´Â ºñ½ÁÇÑ ¼öÁØÀÓÀ» È®ÀÎÇÏ¿´°í Brussels ºÏºÎ¿Í Deurne Áö¿ª¿¡ ºñÇؼ­ Antwerp ³²ºÎ Áö¿ª¿¡¼­ ´ë¸¶¿Í ÄÉŸ¹ÎÀÇ »ç¿ëÀÌ ¸¹´Ù´Â °Íµµ È®ÀÎÇÒ ¼ö ÀÖ¾ú´Ù.
 
º» ¿¬±¸¿¡¼­´Â º§±â¿¡ ³ëµ¿Àý(5¿ù 1ÀÏ)¿¡ ¸Å¿ì °í³óµµÀÇ ÄÉŸ¹Î°ú THC-COOH°¡ °ËÃâµÇ¾ú´Ù´Â »ç½Ç·ÎºÎÅÍ ³ëµ¿ÀýÀ» ÃàÇÏÇϱâ À§ÇÏ¿© »ç¶÷µéÀÌ ºÒ¹ý »ç¿ë±ÝÁö ¾à¹°À» ƯÈ÷ ¸¹ÀÌ »ç¿ëÇÑ´Ù´Â °ÍÀ» È®ÀÎÇÒ ¼ö ÀÖ¾ú´Ù. À̹ø ¿¬±¸Á¶»ç´Â °ø°øº¸°ÇÀÇ À§Ç輺°ú ¿¬°üµÈ ½ÅÁ¾ ¸¶¾à·ùÀÇ È®»ê ¹× ½ÇÅÂÁ¶»ç¿¡ À¯¿ëÇÏ°Ô »ç¿ëµÉ ¼ö ÀÖÀ» °ÍÀÌ´Ù.
 
[Ãâó : KISTI ¹Ì¸®¾È(http://mirian.kisti.re.kr) ¡º±Û·Î¹úµ¿Çâºê¸®ÇÎ(GTB)¡»2013. 03. 18]

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Wastewater drug bonanza: Emerging drugs in treatment plant influent

Wastewater for tracking drug use
Since the original report in 2004, in which unexpectedly high levels of cocaine were discovered in the River Po in Italy, there have been a number of reports of the presence of pharmaceuticals and drugs of abuse in rivers, surface waters and wastewater treatment plants. These studies have been used to gain a rough idea of the trends in drug use in the localities feeding those waters.
 
Any drugs or their metabolites that are excreted by users will be directed to local wastewater treatment plants and this will be a more accurate location for monitoring drug use in the region than rivers or seas, since the wastewater treatment process removes some of the drugs, but obviously not all. In fact, the European Monitoring Centre for Drugs and Drug Addiction acknowledges the use of wastewater as a means of tracking drug use in communities.
 
 
Most of the studies carried out so far have concentrated on the classical drugs of abuse like cocaine, morphine, amphetamines, heroin, and the heroin substitute methadone. Now, Alexander van Nuijs and co-researchers from the University of Antwerp, Belgium, and the University of Bucharest, Romania, have extended the idea to some emerging illicit drugs present in the influent at wastewater treatment plants.
 
They developed and validated a LC-tandem-MS method for the simultaneous measurement of ketamine (KET) and its metabolites norKET and dehydronorKET, the cathinone derivatives methylenedioxypyrovalerone (MDPV) and mephedrone (4-methylmethcathinone, MEPH) and the cannabis metabolite THC-COOH. The method and results were reported in Drug Testing and Analysis.
 
Daily dose
Wastewater influent was collected over a few weeks for periods of 24 hours at a time from three Belgian treatment plants, each with a catchment area of more than 100,000 people living in Brussels and Antwerp. Portions of each were extracted by solid-phase extraction, with a polymeric reversed-phase sorbent outperforming a mixed-mode cation exchange sorbent, largely due to the failure of the latter to retain THC-COOH.
 
The target compounds in the extract were separated on a short reversed-phase C18 column. It was preferred over several other columns because it separated THC-COOH from the remaining analytes, which was preferred because it is detected by mass spectrometry in negative-ion mode while the others are detected in positive-ion mode. This way, only one polarity switch is needed during each run.
 
The chosen column also provided good separation of most of the analytes, eluting them within 8.5 minutes. The peaks for norKET and dehydronorKET partially overlapped but the use of different transitions during multiple reaction monitoring prevented any problems. The total run time, including column equilibration, was just 13 minutes.
 
In the mass spectrometer, the protonated or deprotonated molecules were monitored in each case in multiple reaction monitoring mode, selecting specific product ions to give unique transitions for each analyte. Deuterated analytes were used as internal standards.
 
District variations in drug use
The optimised method gave quantitation limits of 2 ng/L for THC-COOH and 5 ng/L for the remaining drugs and metabolites and the other analytical data were all deemed to be acceptable.
 
When the wastewater influents were tested, THC-COOH and KET were found in samples from all of the treatment plants. NorKET was also detected from its retention time and the observed mass spectral peaks but it was below the detection limit. The remaining three target compounds, dehydronorKET, MEPH and MDPV were not detected.
 
The concentrations of THC-COOH were of the same order as those reported from other studies but the levels of KET were lower than those in Spanish and UK influent wastewater. However, the differences could be due to several factors including variations in the amount of drug consumed in the different regions, sampling times and the stability of the compounds in a particular wastewater treatment plant.
 
The researchers suggested that a better way to compare results from different locations would be to use mass loads which are normalised for the number of inhabitants served by a particular treatment plant. This would reduce any variations due to sampling time and location. In this way, the daily levels for the three Belgian treatment plants were compared.
 
No clear trends were observed for KET or THC-COOH. However, the data revealed more cannabis and ketamine was abused in the Antwerp South region than in Brussels North and Deurne. This conclusion agrees with the results from another study looking at the abuse of cocaine and amphetamines in 19 European studies which saw higher loads for Antwerp South.
 
Another notable occurrence was the high concentrations of KET and THC-COOH on May 1st, which is Labour Day in Belgium. It seems that the residents celebrated this public holiday with a few extra recreational drugs.
 
This method can be used with wastewater treatment plant influent to extend the assessment of illicit drugs to these emerging drugs, helping to identify trends in drug use and the associated public health risks.
 
 
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