Greg Schwab and Lloyd Murdock
Wet soils cause nitrogen losses.  In cases where high intensity rain results 
in high runoff, leaching losses will probably be 
low.  The primary nitrogen loss mechanism in 
saturated soils is denitrification, which occurs 
when soil nitrate nitrogen (NO3-N) is converted 
to nitrogen gas by soil bacteria.  Two to three 
days of soil saturation is required for bacteria to 
begin the denitrification process.  
Well-drained upland soils that have been wet from a series of rains probably have not experienced much 
denitrification.  Soils in lower landscape 
positions that stay saturated longer will likely 
lose more N.  Losses can be calculated by 
estimating 3 to 4 percent loss of fertilizer NO3-N 
for each day of saturation.  Use the Table below 
to determine how much fertilizer NO3-N was in 
the soil. 
EXAMPLE:   Determining the Amount of  
N Loss  
A  farmer  applied  175  lb  nitrogen  (N)/A  as  urea  to  
corn  grown  on  poorly  drained  soil.    Three  weeks  after  application  
the  field  became  saturated  for  seven  days.    How  
much N was lost?  
Step  1.    Determine  the  amount  of  applied  N  
that was in the nitrate (NO3‐N) form.  
According  to  the  table,  50%  of  the  urea  will  be  in  the  
NO3‐N form three weeks after application.  175 lb N x  
50% = 88 lb N.  
Step 2.  Determine the amount of N lost.  
Remember that two days are needed for the bacteria  
to  begin  the  denitrification  process.    Therefore,  
denitrification  occurred  for  five  days  (seven  days  
total  saturation  minus  two  days  to  start  the  process).   
With  4%  lost  each  day  for  five  days,  20%  would  have  
been  lost.    88  lb  N  x  20%  =  18  lb  N  lost  and  157  lb  N  
remaining.      The  N  loss  calculated  in  this  example  is  
not  as  high  as  most  people  would  assume.    A  soil  N  
test can verify this estimation.    
Nitrogen Soil Test  
An  additional  tool  for  determining  NO3‐N  in  the  soil  
after flooding is a NO3‐N test.  The soil sample should  
be  taken  down  to  12  inches  deep,  and  several  
samples should be taken in each field of both the low  
and  higher  ground.    The  samples  should  be  mixed  
well and a subsample sent for nitrate analysis.  
If  the  nitrate‐N  is  less  than  11  ppm,  there  is  a  low  
amount  of  plant‐available  N  in  the  soil.    Therefore,  
there  is  a  good  chance  corn  will  respond  to  a  
sidedress  application  of  N  ranging  from  100  to  150  
lbs N/acre.  
If  the  nitrate‐N  is  between  11  and  25  ppm,  there  is  a  
greater  amount  of  plant‐available  N  in  the  soil,  
indicating  corn  may  or  may  not  respond  to  sidedress  
N.    The  recommended  sidedress  N  application  at  this  
soil  test  level  is  0  to  100  lbs  N/acre.    If  the  soil  test  
nitrate‐N  is  close  to  11  ppm,  then  higher  sidedress  N  
rates  would  be  used.    Lower  rates  would  be  used  as  
nitrate‐N  approaches  25  ppm.    The  test  is  least  
accurate  in  this  range,  so  the  test  results  can  only  be  
used as a broad guide.  
If  soil  test  nitrate‐N  is  greater  than  25  ppm,  there  is  
adequate  plant‐available  N  in  the  soil,  which  
indicates  corn  will  probably  not  respond  to  sidedress  
N application.  
Nitrogen Broadcast Prior to Rain  
Farmers  sometimes  broadcast  fertilizer  nitrogen  on  a  
field  within  24  hours  of  a  heavy  rain.    In  most  cases,  
very  little  nitrogen  is  lost  to  runoff,  especially  if  the  
field  was  under  no‐till  soil  management.    The  
nitrogen  fertilizer  begins  to  dissolve  almost  
immediately  after  being  applied  to  the  soil  surface  
and will dissolve completely in a short period of time.   
As  rain  begins,  the  first  water  that  falls  moves  into  
the  soil,  taking  most  of  the  fertilizer  nitrogen  with  it.   
Once  in  the  soil,  most  of  the  fertilizer  nitrogen  is  
protected  from  runoff.    The  only  exception  is  a  very  
intense  rain  soon  after  application  that  also  erodes  
topsoil  from  sloping  areas.    Even  in  this  situation,  the  
loss  would  probably  be  less  than  one  third  of  the  
fertilizer applied.

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