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Biodegradation of trace organic contaminants in stormwater infiltration systems

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A                       B                         C                    

Figure  1.  Diuron  degradaAon  (A),  DCPMU  generaAon  (B),  and  dichloroaniline  generaAon   (C)  over  the  course  of  the  experiment.  The  parent  compound  concentraAon  (A)  is  

expressed  as  the  raAo  of  the  concentraAon  in  the  bioAc  microcosms    to  the  

concentraAon  in  the  inacAvated  microcosms  to  observes  effects  due  to  biodegradaAon   only.    This  raAo  was  normalized,  such  that  a  raAo  below  1  indicates  biodegradaAon.  

 

ObservaAons:  

•  More  degradaAon  with  microcosms  with  added  DOC    

•  Higher  transformaAon  product  concentraAons  were  observed  in  the  

microcosms  using  compost  as  a  DOC  source  

•  Dichloroaniline  is  generated,  which  is  more  toxic  and  mobile  than  DCPMU  

                                       

BiodegradaCon  of  Trace  Organic  Contaminants  in  Stormwater  InfiltraCon  Systems  

Katelynn  J.  Edgehouse1-­‐3;  Bridget  A.  Ulrich2,3;  Christopher  P.  Higgins,  PhD2  

1Cleveland  State  University,  2Colorado  School  of  Mines,  3  Re-­‐InvenAng  the  NaAon’s  Urban  Water  Infrastructure  

UrbanizaAon  has  degraded  water  resources,  in  part  due  to  poor  management   of  stormwater  runoff.  Stormwater  runoff  takes  up  trace  organic  contaminants   (TOrCs)  from  urban  surfaces,  which  contaminate  urban  receiving  waters.  With   water  quality  and  quanAty  becoming  increasingly  pressing,  it  is  important  that   the  water  resources  currently  available  are  relaAvely  free  of  contaminants.  

There  are  some  methods  currently  in  place  to  try  to  miAgate  the  affects  of   stormwater  runoff  entering  urban  receiving  waters,  but  these  pracAces  are   not  always  effecAve.  For  example,  most  rain  gardens  have  sand  as  their  base,   and  polar  TOrCs  filter  through  the  sand  instead  of  being  sorbed  and  

potenAally  degraded.    

Diuron  DegradaCon  and  TransformaCon  Product  GeneraCon  

Hypothesis:  The  type  of  carbon  source  added  to  a  stormwater  infiltraAon  basin  will   have  an  effect  on  TOrC  biodegradaAon  rates  and  transformaAon  products  

Tasks:  

•  Asses  degradaAon  rates  of  parent  TOrCs  in  microcosms  represenAng  

stormwater  infilitraAon  systems  

•  IdenAfy  transformaAon  products  of  the  parent  TOrCs  

   

Goals  

•  30  microcosms  were  created  to  simulate  different  stormwater  infiltraAon  

systems  

•  Samples  were  taken  from  the  microcosms  weekly,  and  then  targeted  analysis  of  

the  parent  TOrCs  was  done  via  liquid  chromatography  tandem  mass  

spectrometry  (LC-­‐MS/MS(  to  monitor  degradaAon  and  some  transformaAon   product  appearance.  

•  Once  significant  degradaAon  had  occurred,  non-­‐targeted  analysis  for  

transformaAon  products  was  done  using  LC-­‐QTOF-­‐MS.  

Approach   A                   B                   C                    

Figure  2.  Atrazine  degradaAon  (A),  atrazine  desisopropyl  generaAon  (B),  and  atrazine   desethyl  (C)  over  the  course  of  the  experiment.  

 

ObservaAons:  

•  Unlike  diuron,  less  difference  in  removal  for  added  DOC  relaAve  to  runoff  

(no  added  DOC).  

•  Like  diuron,  more  transformaAon  products  generated  in  the  compost  

microcosms.                                                  

Atrazine  DegradaCon  and  TransformaCon  Product  GeneraCon  

Kate  Edgehouse  

Cleveland  State  University  

Email:  k.j.edgehouse@vikes.csuohio.edu   Phone:  (440)  840-­‐5280   Contact  

 

 

 

     

•  InacAvated  microcosms  contained  sodium  azide  to  prevent  biodegradaAon    

•  Runoff  only  microcosms  had  no  added    source  of  dissolved  organic  carbon  

(DOC).  

•  TOrCs  were  spiked  into  microcosms  at  a  level  of  50  ppb.  

•  TOrC  concentraAons  were  monitored  by  LC-­‐MS/MS  

Microcosm  Set  -­‐  Up  

InacAvated   InacAvated   InacAvated  

BioAc   BioAc   BioAc   x5   x5   x5   x5   x5   x5   0   0.2   0.4   0.6   0.8   1   1.2   1.4   1.6   0   5   10   15   20   25   30   35   40   [BioC c]/[Inac Cvate d]   Time  (Days)   Compost   Straw  

No  Added  DOC  

-­‐0.5   0   0.5   1   1.5   2   2.5   3   3.5   4   0   5   10   15   20   25   30   35   40   Co ncen tra Co n  ( μg/ L   )   Time  (Days)   Compost   Straw  

No  Added  DOC  

0   0.1   0.2   0.3   0.4   0.5   0.6   0   5   10   15   20   25   30   35   40   Co ncen tra Co n  ( μg/ L   )   Time  (Days)   Compost   Straw  

No  Added  DOC  

0   0.2   0.4   0.6   0.8   1   1.2   1.4   0   5   10   15   20   25   30   35   40   45   [BioC c]/[Inac Cvate d]   Time  (Days)   Compost   Straw  

No  Added  DOC  

0   0.5   1   1.5   2   2.5   0   5   10   15   20   25   30   35   40   Co ncen tra Co n  ( μg/ L   )   Time  (Days)   Compost   Straw  

No  Added  DOC  

0   0.5   1   1.5   2   2.5   0   5   10   15   20   25   30   35   40   Co ncen tra Co n  ( μg/ L   )   Time  (Days)   Compost   Straw  

No  Added  DOC  

•  Carbon  source  does  affect  TOrC  biodegradaAon  

•  More  transformaAon  products  appeared  to  be  generated  in  the  

microcosms  with  compost  as  a  DOC  source  

•  Knowing  which  transformaAon  products  the  TOrCs  are  generated  is  

important  because  someAmes  the  transformaAon  product  is  more   toxic  than  its  parent  TOrC.  

References

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