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Forest Canopy Coverage Adjacent to Forest Roads
and its Effect on Invasive Plant Species

Beth Lewis and Sherry Wood
Department of Biology, Gonzaga University, Spokane, Washington
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Introduc)on	
  
Methods	
  
Results	
   Conclusions	
  and	
  Future	
  Work	
  
State	
  and	
  Federal	
  Agencies	
  manage	
  forest	
  roads	
  in	
  order	
  to	
  provide	
  
access	
  for	
  forest	
  use	
  to	
  the	
  public.	
  Employees	
  monitor	
  the	
  spread	
  of	
  
invasive	
  weed	
  species	
  that	
  overrun	
  roadsides	
  and	
  outcompete	
  
nave	
  plant	
  species.	
  Invasive	
  weed	
  species	
  are	
  alien	
  species	
  whose	
  
introducon	
  does	
  or	
  is	
  likely	
  to	
  cause	
  environmental	
  harm.	
  The	
  
Idaho	
  Panhandle	
  Naonal	
  Forest	
  (IPNF)	
  contains	
  2.5	
  million	
  acres	
  
and	
  has	
  over	
  11,000	
  miles	
  of	
  roads.	
  The	
  Coeur	
  d’Alene	
  River	
  District	
  
in	
  northern	
  Idaho	
  spends	
  $25.50	
  per	
  acre	
  of	
  road	
  spraying	
  roadsides	
  
with	
  herbicides	
  to	
  inhibit	
  invasive	
  plant	
  species.	
  If	
  the	
  Forest	
  Service	
  
were	
  to	
  spray	
  every	
  road	
  throughout	
  the	
  IPNF,	
  they	
  would	
  be	
  
spending	
  over	
  1.5	
  million	
  dollars	
  a	
  year	
  on	
  herbicide	
  treatment.	
  	
  
	
  
Managing	
  invasive	
  weed	
  species	
  is	
  incredibly	
  important	
  due	
  to	
  the	
  
detrimental	
  effects	
  on	
  the	
  environment	
  and	
  the	
  toxicity	
  the	
  plants	
  
have	
  on	
  nave	
  animals.	
  (DiTomaso,	
  2000)	
  Connuing	
  to	
  spray	
  the	
  
roadsides	
  with	
  herbicides	
  influences	
  not	
  only	
  the	
  invasive	
  weeds,	
  
but	
  also	
  may	
  damage	
  nave	
  species.	
  (Rinella	
  et	
  al.	
  2009)	
  An	
  
alternave	
  way	
  of	
  reducing	
  the	
  abundance	
  of	
  invasive	
  weed	
  species	
  
was	
  studied	
  by	
  a	
  team	
  of	
  research	
  students	
  who	
  collected	
  data	
  on	
  
forest	
  canopy	
  coverage	
  and	
  invasive	
  weed	
  species	
  presence.	
  Canopy	
  
coverage	
  is	
  the	
  percentage	
  of	
  the	
  forest	
  floor	
  covered	
  by	
  the	
  vercal	
  
projecon	
  of	
  the	
  tree	
  crowns.	
  If	
  canopy	
  coverage	
  has	
  a	
  negave	
  
impact	
  on	
  invasive	
  weed	
  species,	
  keeping	
  roads	
  narrower	
  would	
  
minimize	
  the	
  herbicides	
  needed	
  to	
  manage	
  invasive	
  species.	
  
	
  
As	
  forest	
  canopy	
  coverage	
  increases	
  the	
  presence	
  of	
  invasive	
  weed	
  
species	
  will	
  decrease.	
  
Roads	
  in	
  the	
  IPNF	
  in	
  the	
  Coeur	
  d’Alene	
  River	
  watershed	
  were	
  
selected	
  and	
  each	
  assigned	
  around	
  fiVy	
  random	
  points	
  distributed	
  
within	
  7	
  meters	
  on	
  either	
  side	
  of	
  the	
  roads	
  centerline.	
  610	
  plots	
  
were	
  recorded.	
  The	
  roads	
  were	
  all	
  heterogeneous	
  in	
  nature	
  and	
  
differed	
  in	
  roadside	
  canopy	
  coverage,	
  elevaon,	
  treatment	
  and	
  fire	
  
history.	
  Each	
  point	
  was	
  found	
  using	
  GPS	
  coordinates.	
  A	
  one-­‐meter	
  
by	
  one-­‐meter	
  plot	
  was	
  laid	
  down	
  at	
  the	
  coordinate	
  site	
  and	
  every	
  
plant	
  species	
  within	
  the	
  plot	
  was	
  recorded	
  and	
  the	
  percent	
  coverage	
  
was	
  esmated	
  using	
  Daubenmire	
  Cover	
  Classes.	
  A	
  spherical	
  
densiometer	
  was	
  used	
  to	
  record	
  the	
  canopy	
  coverage	
  of	
  	
  
the	
  tree	
  crowns	
  directly	
  	
  
overhead	
  the	
  plots.	
  
JMP	
  12.0	
  was	
  used	
  to	
  examine	
  
the	
  relaonship	
  between	
  	
  
forest	
  canopy	
  coverage	
  and	
  
the	
  percent	
  cover	
  of	
  invasive	
  	
  
weed	
  species	
  adjacent	
  to	
  the	
  	
  
forest	
  roads.	
  	
  
Forest	
  canopy	
  coverage	
  percentage	
  was	
  compared	
  to	
  each	
  of	
  the	
  different	
  invasive	
  weed	
  
species.	
  Only	
  two	
  of	
  the	
  seven	
  plants	
  we	
  studied	
  showed	
  a	
  significant	
  relaonship	
  
between	
  canopy	
  coverage	
  and	
  invasive	
  weed	
  species	
  percentage.	
  Figures	
  1	
  and	
  2	
  had	
  a	
  
negave	
  sloping	
  trend	
  showing	
  as	
  the	
  percent	
  canopy	
  coverage	
  increases	
  the	
  invasive	
  
weed	
  species	
  presence	
  decreases.	
  Figure	
  1	
  shows	
  canopy	
  coverage	
  compared	
  to	
  St.	
  Johns	
  
Wort	
  with	
  a	
  p-­‐value	
  less	
  than	
  0.001	
  indicang	
  a	
  high	
  significance.	
  Figure	
  2	
  shows	
  canopy	
  
coverage	
  compared	
  to	
  oxeye	
  daisy	
  with	
  a	
  p-­‐value	
  of	
  0.0166	
  also	
  indicang	
  significance.	
  
	
  
The	
  other	
  five	
  weed	
  species,	
  Spo^ed	
  Knapweed,	
  Meadow	
  Hawkweed	
  showed	
  no	
  
correlaon	
  between	
  canopy	
  coverage	
  and	
  invasive	
  weed	
  species.	
  When	
  we	
  looked	
  at	
  the	
  
sum	
  of	
  all	
  seven	
  invasive	
  weed	
  species	
  compared	
  to	
  the	
  percent	
  canopy	
  coverage	
  per	
  
plot,	
  we	
  see	
  there	
  is	
  a	
  significant	
  difference	
  between	
  plots	
  with	
  high	
  canopy	
  coverage	
  and	
  
low	
  canopy	
  coverage.	
  Figure	
  3	
  shows	
  plots	
  with	
  a	
  high	
  percentage	
  canopy	
  coverage	
  
generally	
  had	
  a	
  lower	
  amount	
  of	
  invasive	
  weed	
  species	
  present	
  in	
  the	
  plot.	
  The	
  p-­‐value	
  is	
  
less	
  than	
  0.001	
  indicang	
  a	
  high	
  significant	
  difference.	
  Although	
  the	
  majority	
  of	
  the	
  
invasive	
  weeds	
  were	
  not	
  significantly	
  affected	
  by	
  canopy	
  coverage,	
  the	
  high	
  significance	
  
of	
  St.	
  Johns	
  Word	
  and	
  Oxeye	
  Daisy	
  overpowered	
  the	
  non-­‐significant	
  comparisons.	
  
	
  
Invasive	
  weed	
  species	
  move	
  into	
  forests	
  through	
  moving	
  along	
  road	
  corridors.	
  (Pauchard,	
  
2004)	
  If	
  road	
  corridors	
  were	
  kept	
  narrower	
  with	
  higher	
  canopy	
  coverage	
  along	
  them,	
  we	
  
could	
  expect	
  fewer	
  invasive	
  weed	
  species	
  would	
  grow	
  along	
  the	
  roadsides.	
  Herbicides	
  
can	
  connually	
  be	
  used	
  as	
  a	
  method	
  to	
  treat	
  invasive	
  weed	
  species	
  however,	
  studies	
  
show	
  that	
  they	
  can	
  become	
  resistant	
  to	
  herbicide	
  treatment	
  in	
  20	
  generaons.	
  (Prens,	
  
2008)	
  By	
  keeping	
  the	
  roads	
  shaded,	
  there	
  is	
  a	
  higher	
  chance	
  that	
  herbicides	
  will	
  not	
  be	
  
essenal	
  in	
  management	
  of	
  invasive	
  weed	
  species	
  allowing	
  the	
  Forest	
  Service	
  to	
  use	
  the	
  
money	
  to	
  benefit	
  other	
  aspects	
  of	
  the	
  forest.	
  
	
  
Sources	
  of	
  Error:	
  
Error	
  could	
  come	
  from	
  a	
  few	
  different	
  factors.	
  When	
  recording	
  the	
  percent	
  canopy	
  
coverage	
  with	
  the	
  spherical	
  densiometer,	
  if	
  the	
  same	
  person	
  did	
  not	
  take	
  the	
  
measurement	
  each	
  me,	
  there	
  could	
  be	
  a	
  difference	
  in	
  their	
  technique,	
  increasing	
  a	
  
chance	
  of	
  error.	
  Another	
  error	
  factor	
  could	
  come	
  from	
  different	
  people	
  assigning	
  cover	
  
classes	
  to	
  the	
  different	
  weeds	
  in	
  each	
  plot.	
  These	
  could	
  have	
  affected	
  the	
  overall	
  results,	
  
causing	
  a	
  gain	
  or	
  loss	
  in	
  significance	
  between	
  canopy	
  coverage	
  and	
  invasive	
  weed	
  species.	
  
	
  
Future	
  Work:	
  
Connuing	
  this	
  project	
  would	
  provide	
  vital	
  informaon	
  for	
  the	
  Forest	
  Service	
  so	
  they	
  can	
  
connue	
  to	
  manage	
  the	
  roads	
  in	
  the	
  most	
  efficient	
  way	
  possible.	
  By	
  taking	
  into	
  account	
  
elevaon	
  and	
  herbicide	
  treatments	
  a	
  more	
  comprehensive	
  conclusion	
  on	
  canopy	
  
coverage	
  effect	
  could	
  be	
  made.	
  
	
  
	
  
	
  	
  References	
  and	
  Acknowledgements	
  
Thank	
  you	
  to	
  Sherry	
  Wood	
  for	
  aiding	
  in	
  project	
  development	
  and	
  supervision.	
  Forest	
  Service	
  employee	
  Gilbert	
  Moreno	
  aided	
  in	
  
idenficaon	
  of	
  endless	
  plants.	
  
This	
  research	
  was	
  supported	
  in	
  part	
  by	
  a	
  grant	
  to	
  Gonzaga	
  University	
  from	
  the	
  Howard	
  Hughes	
  Medical	
  Instute	
  through	
  the	
  
Undergraduate	
  Science	
  Educaon	
  Program.	
  
DiTomaso,	
  J	
  (2000,)	
  Invasive	
  weeds	
  in	
  rangelands:	
  Species,	
  impacts,	
  and	
  management.	
  Weed	
  Science:	
  March	
  2000,	
  Vol.	
  48,	
  No.	
  2,	
  pp.	
  255-­‐265.	
  
Pauchard,	
  A.	
  and	
  Alaback,	
  P.	
  B.	
  (2004),	
  Influence	
  of	
  Elevaon,	
  Land	
  Use,	
  and	
  Landscape	
  Context	
  on	
  Pa^erns	
  of	
  Alien	
  Plant	
  Invasions	
  along	
  Roadsides	
  in	
  
Protected	
  Areas	
  of	
  South-­‐Central	
  Chile.	
  Conservaon	
  Biology,	
  18:	
  238–248.	
  
Prens,	
  P.,	
  Wilson,	
  R.	
  et	
  al.	
  (2008)	
  Adapve	
  evoluon	
  in	
  invasive	
  species,	
  Trends	
  in	
  Plant	
  Science,	
  Volume	
  13,	
  Issue	
  6,	
  Pages	
  288-­‐294,	
  ISSN	
  1360-­‐1385	
  
Rinella,	
  M.	
  J.,	
  Maxwell,	
  B.	
  D.,	
  Fay,	
  P.	
  K.,	
  Weaver,	
  T.	
  and	
  Sheley,	
  R.	
  L.	
  (2009),	
  Control	
  effort	
  exacerbates	
  invasive-­‐species	
  problem.	
  Ecological	
  Applicaons,	
  
19:	
  155–162.	
  doi:10.1890/07-­‐1482.1	
  
	
  
Figure	
  2:	
  Bivariate	
  Fit	
  of	
  Oxeye	
  Daisy	
  by	
  Percent	
  
Canopy	
  Coverage	
  
The	
  comparison	
  of	
  the	
  percent	
  forest	
  canopy	
  coverage	
  
in	
  a	
  plot	
  versus	
  the	
  percent	
  coverage	
  of	
  Oxeye	
  Daisy.	
  
The	
  p-­‐value	
  is	
  0.0166	
  indicang	
  a	
  significant	
  negave	
  
relaonship	
  between	
  canopy	
  coverage	
  and	
  percent	
  
coverage	
  of	
  Oxeye	
  Daisy.	
  
Figure	
  3:	
  Bivariate	
  Fit	
  of	
  Sum	
  of	
  Weed	
  Coverage	
  by	
  	
  
Percent	
  Canopy	
  Coverage	
  
The	
  comparison	
  of	
  percent	
  forest	
  canopy	
  coverage	
  in	
  
a	
  plot	
  versus	
  the	
  total	
  sum	
  of	
  invasive	
  weed	
  coverage	
  
percentages	
  per	
  plot.	
  The	
  p-­‐value	
  is	
  less	
  than	
  0.001	
  
indicang	
  a	
  significant	
  negave	
  relaonship	
  between	
  
canopy	
  coverage	
  and	
  the	
  total	
  invasive	
  weed	
  species	
  
coverage.	
  
	
  
Figure	
  1:	
  Bivariate	
  Fit	
  of	
  St.	
  Johns	
  Wort	
  by	
  Percent	
  
Canopy	
  Coverage	
  
The	
  comparison	
  of	
  the	
  percent	
  forest	
  canopy	
  coverage	
  
in	
  a	
  plot	
  versus	
  the	
  percent	
  coverage	
  of	
  St.	
  John’s	
  
Wort.	
  The	
  p-­‐value	
  is	
  less	
  than	
  0.001	
  indicang	
  a	
  
significant	
  negave	
  relaonship	
  between	
  canopy	
  
coverage	
  and	
  percent	
  coverage	
  of	
  St.	
  John’s	
  Wort.	
  
Figure	
  4:	
  Bivariate	
  Fit	
  of	
  SpoNed	
  Knapweed	
  by	
  
Percent	
  Canopy	
  Coverage	
  
The	
  comparison	
  of	
  percent	
  forest	
  canopy	
  coverage	
  in	
  a	
  
plot	
  versus	
  the	
  percent	
  coverage	
  of	
  Spo^ed	
  
Knapweed.	
  Although	
  there	
  is	
  a	
  negave	
  linear	
  fit	
  line,	
  
the	
  p-­‐value	
  is	
  0.5535	
  indicang	
  there	
  is	
  not	
  a	
  
significant	
  negave	
  relaonship	
  between	
  canopy	
  
coverage	
  and	
  percent	
  coverage	
  of	
  Spo^ed	
  Knapweed.	
  
Figure	
  5:	
  Roadside	
  Covered	
  by	
  Invasive	
  Weed	
  Species	
  
A	
  roadside	
  covered	
  by	
  invasive	
  weeds	
  with	
  li^le	
  canopy	
  
coverage.	
  St.	
  John’s	
  Wort	
  is	
  the	
  most	
  prevalent	
  weed.	
  
Photo	
  was	
  taken	
  standing	
  in	
  the	
  middle	
  of	
  the	
  road.	
  	
  
Figure	
  6:	
  Roadside	
  with	
  High	
  Canopy	
  Coverage	
  
A	
  roadside	
  with	
  high	
  forest	
  canopy	
  coverage	
  and	
  li^le	
  
invasive	
  weed	
  species	
  presence.	
  Photo	
  was	
  taken	
  
standing	
  in	
  the	
  middle	
  of	
  the	
  road.	
  

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Poster Presentation FS Canopy Coverage As PDF

  • 1. Forest Canopy Coverage Adjacent to Forest Roads and its Effect on Invasive Plant Species Beth Lewis and Sherry Wood Department of Biology, Gonzaga University, Spokane, Washington 1.5 kb 1 kb Introduc)on   Methods   Results   Conclusions  and  Future  Work   State  and  Federal  Agencies  manage  forest  roads  in  order  to  provide   access  for  forest  use  to  the  public.  Employees  monitor  the  spread  of   invasive  weed  species  that  overrun  roadsides  and  outcompete   nave  plant  species.  Invasive  weed  species  are  alien  species  whose   introducon  does  or  is  likely  to  cause  environmental  harm.  The   Idaho  Panhandle  Naonal  Forest  (IPNF)  contains  2.5  million  acres   and  has  over  11,000  miles  of  roads.  The  Coeur  d’Alene  River  District   in  northern  Idaho  spends  $25.50  per  acre  of  road  spraying  roadsides   with  herbicides  to  inhibit  invasive  plant  species.  If  the  Forest  Service   were  to  spray  every  road  throughout  the  IPNF,  they  would  be   spending  over  1.5  million  dollars  a  year  on  herbicide  treatment.       Managing  invasive  weed  species  is  incredibly  important  due  to  the   detrimental  effects  on  the  environment  and  the  toxicity  the  plants   have  on  nave  animals.  (DiTomaso,  2000)  Connuing  to  spray  the   roadsides  with  herbicides  influences  not  only  the  invasive  weeds,   but  also  may  damage  nave  species.  (Rinella  et  al.  2009)  An   alternave  way  of  reducing  the  abundance  of  invasive  weed  species   was  studied  by  a  team  of  research  students  who  collected  data  on   forest  canopy  coverage  and  invasive  weed  species  presence.  Canopy   coverage  is  the  percentage  of  the  forest  floor  covered  by  the  vercal   projecon  of  the  tree  crowns.  If  canopy  coverage  has  a  negave   impact  on  invasive  weed  species,  keeping  roads  narrower  would   minimize  the  herbicides  needed  to  manage  invasive  species.     As  forest  canopy  coverage  increases  the  presence  of  invasive  weed   species  will  decrease.   Roads  in  the  IPNF  in  the  Coeur  d’Alene  River  watershed  were   selected  and  each  assigned  around  fiVy  random  points  distributed   within  7  meters  on  either  side  of  the  roads  centerline.  610  plots   were  recorded.  The  roads  were  all  heterogeneous  in  nature  and   differed  in  roadside  canopy  coverage,  elevaon,  treatment  and  fire   history.  Each  point  was  found  using  GPS  coordinates.  A  one-­‐meter   by  one-­‐meter  plot  was  laid  down  at  the  coordinate  site  and  every   plant  species  within  the  plot  was  recorded  and  the  percent  coverage   was  esmated  using  Daubenmire  Cover  Classes.  A  spherical   densiometer  was  used  to  record  the  canopy  coverage  of     the  tree  crowns  directly     overhead  the  plots.   JMP  12.0  was  used  to  examine   the  relaonship  between     forest  canopy  coverage  and   the  percent  cover  of  invasive     weed  species  adjacent  to  the     forest  roads.     Forest  canopy  coverage  percentage  was  compared  to  each  of  the  different  invasive  weed   species.  Only  two  of  the  seven  plants  we  studied  showed  a  significant  relaonship   between  canopy  coverage  and  invasive  weed  species  percentage.  Figures  1  and  2  had  a   negave  sloping  trend  showing  as  the  percent  canopy  coverage  increases  the  invasive   weed  species  presence  decreases.  Figure  1  shows  canopy  coverage  compared  to  St.  Johns   Wort  with  a  p-­‐value  less  than  0.001  indicang  a  high  significance.  Figure  2  shows  canopy   coverage  compared  to  oxeye  daisy  with  a  p-­‐value  of  0.0166  also  indicang  significance.     The  other  five  weed  species,  Spo^ed  Knapweed,  Meadow  Hawkweed  showed  no   correlaon  between  canopy  coverage  and  invasive  weed  species.  When  we  looked  at  the   sum  of  all  seven  invasive  weed  species  compared  to  the  percent  canopy  coverage  per   plot,  we  see  there  is  a  significant  difference  between  plots  with  high  canopy  coverage  and   low  canopy  coverage.  Figure  3  shows  plots  with  a  high  percentage  canopy  coverage   generally  had  a  lower  amount  of  invasive  weed  species  present  in  the  plot.  The  p-­‐value  is   less  than  0.001  indicang  a  high  significant  difference.  Although  the  majority  of  the   invasive  weeds  were  not  significantly  affected  by  canopy  coverage,  the  high  significance   of  St.  Johns  Word  and  Oxeye  Daisy  overpowered  the  non-­‐significant  comparisons.     Invasive  weed  species  move  into  forests  through  moving  along  road  corridors.  (Pauchard,   2004)  If  road  corridors  were  kept  narrower  with  higher  canopy  coverage  along  them,  we   could  expect  fewer  invasive  weed  species  would  grow  along  the  roadsides.  Herbicides   can  connually  be  used  as  a  method  to  treat  invasive  weed  species  however,  studies   show  that  they  can  become  resistant  to  herbicide  treatment  in  20  generaons.  (Prens,   2008)  By  keeping  the  roads  shaded,  there  is  a  higher  chance  that  herbicides  will  not  be   essenal  in  management  of  invasive  weed  species  allowing  the  Forest  Service  to  use  the   money  to  benefit  other  aspects  of  the  forest.     Sources  of  Error:   Error  could  come  from  a  few  different  factors.  When  recording  the  percent  canopy   coverage  with  the  spherical  densiometer,  if  the  same  person  did  not  take  the   measurement  each  me,  there  could  be  a  difference  in  their  technique,  increasing  a   chance  of  error.  Another  error  factor  could  come  from  different  people  assigning  cover   classes  to  the  different  weeds  in  each  plot.  These  could  have  affected  the  overall  results,   causing  a  gain  or  loss  in  significance  between  canopy  coverage  and  invasive  weed  species.     Future  Work:   Connuing  this  project  would  provide  vital  informaon  for  the  Forest  Service  so  they  can   connue  to  manage  the  roads  in  the  most  efficient  way  possible.  By  taking  into  account   elevaon  and  herbicide  treatments  a  more  comprehensive  conclusion  on  canopy   coverage  effect  could  be  made.          References  and  Acknowledgements   Thank  you  to  Sherry  Wood  for  aiding  in  project  development  and  supervision.  Forest  Service  employee  Gilbert  Moreno  aided  in   idenficaon  of  endless  plants.   This  research  was  supported  in  part  by  a  grant  to  Gonzaga  University  from  the  Howard  Hughes  Medical  Instute  through  the   Undergraduate  Science  Educaon  Program.   DiTomaso,  J  (2000,)  Invasive  weeds  in  rangelands:  Species,  impacts,  and  management.  Weed  Science:  March  2000,  Vol.  48,  No.  2,  pp.  255-­‐265.   Pauchard,  A.  and  Alaback,  P.  B.  (2004),  Influence  of  Elevaon,  Land  Use,  and  Landscape  Context  on  Pa^erns  of  Alien  Plant  Invasions  along  Roadsides  in   Protected  Areas  of  South-­‐Central  Chile.  Conservaon  Biology,  18:  238–248.   Prens,  P.,  Wilson,  R.  et  al.  (2008)  Adapve  evoluon  in  invasive  species,  Trends  in  Plant  Science,  Volume  13,  Issue  6,  Pages  288-­‐294,  ISSN  1360-­‐1385   Rinella,  M.  J.,  Maxwell,  B.  D.,  Fay,  P.  K.,  Weaver,  T.  and  Sheley,  R.  L.  (2009),  Control  effort  exacerbates  invasive-­‐species  problem.  Ecological  Applicaons,   19:  155–162.  doi:10.1890/07-­‐1482.1     Figure  2:  Bivariate  Fit  of  Oxeye  Daisy  by  Percent   Canopy  Coverage   The  comparison  of  the  percent  forest  canopy  coverage   in  a  plot  versus  the  percent  coverage  of  Oxeye  Daisy.   The  p-­‐value  is  0.0166  indicang  a  significant  negave   relaonship  between  canopy  coverage  and  percent   coverage  of  Oxeye  Daisy.   Figure  3:  Bivariate  Fit  of  Sum  of  Weed  Coverage  by     Percent  Canopy  Coverage   The  comparison  of  percent  forest  canopy  coverage  in   a  plot  versus  the  total  sum  of  invasive  weed  coverage   percentages  per  plot.  The  p-­‐value  is  less  than  0.001   indicang  a  significant  negave  relaonship  between   canopy  coverage  and  the  total  invasive  weed  species   coverage.     Figure  1:  Bivariate  Fit  of  St.  Johns  Wort  by  Percent   Canopy  Coverage   The  comparison  of  the  percent  forest  canopy  coverage   in  a  plot  versus  the  percent  coverage  of  St.  John’s   Wort.  The  p-­‐value  is  less  than  0.001  indicang  a   significant  negave  relaonship  between  canopy   coverage  and  percent  coverage  of  St.  John’s  Wort.   Figure  4:  Bivariate  Fit  of  SpoNed  Knapweed  by   Percent  Canopy  Coverage   The  comparison  of  percent  forest  canopy  coverage  in  a   plot  versus  the  percent  coverage  of  Spo^ed   Knapweed.  Although  there  is  a  negave  linear  fit  line,   the  p-­‐value  is  0.5535  indicang  there  is  not  a   significant  negave  relaonship  between  canopy   coverage  and  percent  coverage  of  Spo^ed  Knapweed.   Figure  5:  Roadside  Covered  by  Invasive  Weed  Species   A  roadside  covered  by  invasive  weeds  with  li^le  canopy   coverage.  St.  John’s  Wort  is  the  most  prevalent  weed.   Photo  was  taken  standing  in  the  middle  of  the  road.     Figure  6:  Roadside  with  High  Canopy  Coverage   A  roadside  with  high  forest  canopy  coverage  and  li^le   invasive  weed  species  presence.  Photo  was  taken   standing  in  the  middle  of  the  road.