Section 319
NDNPDINT SOURC* PROGRAM SUCCESS STDRY
 BMPs Result in Significant Reduction of Bacteria and Phosphorus

 Loading


WatPrhndv Imnrnvpd  Beaty Creek, in northeast Oklahoma, was impaired for patho-
                             gens, specifically E coA'and Enterococcus, due in part to poor
 waste management practices and direct access of livestock to the stream. Landowner educa-
 tion and implementing best management practices (BMPs) to promote proper animal waste
 and nutrient management, as well as better riparian zone management have led to signifi-
 cantly decreased amounts of bacteria in the creek. As a result, Oklahoma expects to remove
 Beaty Creek from its 2006 303(d) list for E coli impairment. In addition, expected phosphorus
 loading to Beaty Creek is also decreasing as compared to a control watershed with no BMP
 implementation.


 Problem

 The Beaty Creek watershed contains approxi-
 mately 39 chicken houses; hog and turkey
 operations; and extensive, streamside cattle
 grazing on pasture fertilized with animal waste.
 Septic systems, land development, some row
 crop agriculture and fertilizer application are
 also found in the watershed. These activities
 have cumulatively generated a high amount
 of nonpoint source pollution and resulted in
 elevated levels of bacteria in Beaty Creek. In
 2002, Oklahoma placed all 13 miles of Beaty
 Creek on the 303(d) list as impaired for E. coli
 and Enterococcus. In addition, high levels of
 phosphorus loading contributed to eutrophi-
 cation and phosphorus exceedance in Lake
 Eucha, a downstream reservoir.


 Project Highlights

 The number one restoration priority for the
 Beaty Creek area was riparian  buffer estab-
 lishment and protection. Another focus was
 disseminating information on pasture manage-
 ment and proper application of poultry litter
 as fertilizer—key issues in the watershed.
 Numerous educational workshops, meet-
 ings, and tours demonstrating BMPs in the
 watershed were essential for the success
                           Areas for cattle feeding and waste storage
                           were constructed to reduce the amount of
                           bacteria and nutrients entering the stream.


                           of this project. Approximately 63 percent of
                           landowners in the watershed implemented
                           BMPs through cost-share contracts from 2000
                           to 2004.
                           Results
                           Attendance was high at the various educational
                           presentations. Approximately 100 cost-share
                           contracts to implement BMPs in the Beaty
                           Creek watershed were signed into action in
                           both Oklahoma and Arkansas. BMPs included
                           establishing 335 acres of riparian buffer

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areas, establishing/managing approximately
10,000 acres of pasture; the provision of more
than 150 alternative water sources for cattle;
the construction of 56 heavy use areas, 16 cat-
tle feeding/waste storage facilities, 31 miles
of cross fencing, four poultry waste storage
facilities; and the replacement of 27 septic
systems. Resulting water quality improve-
ments led to Beaty Creek being nominated for
removal from the 2006 303(d) list forf. coli.
This brings it one step closer to full attainment
of the Primary Body Contact Recreation (PBCR)
beneficial use.

In addition, BMPs have reduced the expected
loading of phosphorus in the Beaty Creek
watershed as compared to a control water-
shed with no BMPs. Analysis of water quality
data collected after the implementation of the
Beaty Creek BMPs indicates that the increas-
ing  trend is no longer evident, which, in itself,
is a measure of success. Independent analysis
of water quality data,  conducted by Oklahoma
State University, using a paired watershed
methodology showed a 31  percent decrease
in expected phosphorus loading to the lake
from Beaty Creek in the presence of BMPs,
compared to expected loading in the absence
of BMPs. Average flow-weighted phosphorus
concentrations decreased from 0.220 mg/L to
0.191 mg/L. Although phosphorus loadings are
still significant, the rate of phosphorus loading
has been reduced. BMP implementation to
reduce nutrient loading and evaluation of the
stream continues.
The success of this project and continued
interest in implementing BMPs has allowed
the pursuit of a related project in the adjoining
Spavinaw Creek watershed. One of the great-
est successes of the project is that landown-
ers are beginning to implement the practices
without the benefit of cost-share assistance,
and they  are requesting assistance with BMP
design and using their own funds. Even land-
owners outside the watershed are interested in
the practices that were demonstrated  in Beaty
Creek and are beginning to implement them.
Partners and Funding
A total of $1,338,401 was available to sup-
port installation of the BMPs associated with
this project. This included $632,467 federal
dollars from EPA section 319 funds,  $528,133
state dollars, and a required $177,800 match
from landowners. The Eucha watershed has
been a special emphasis area for Oklahoma's
EQIP program, ensuring that at least $325,000
worth of additional practices were imple-
mented  throughout the watershed. Different
groups participating in the Beaty Creek
project included the Oklahoma Conservation
Commission,  Delaware County, Oklahoma
and Benton County, Arkansas Conservation
Districts, Oklahoma Department of Agriculture,
Oklahoma State University Cooperative
Extension Service, NRCS, Farm Services
Agency, Arkansas Soil and Water Conservation
Commission,  local producers, poultry integra-
tors, and animal waste marketers.

sou


E 600-
o
o
^™
Colonies/
1 1
o-
£. coli

Geometric mean=115





Geometric mean=25
*
*

P ±
^ i



800-

600-

400-
200-
o-
Enterococcus


Geometric mean=274






*
Geometric mean =76



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*
*
*


'
                                                                      Boxplots indicate the
                                                                      interquartile range
                                                                      (25th-75th percentile)and
                                                                      median of the data in
                                                                      each of two periods: "Pre"
                                                                      contains data from August
                                                                      1999 to January 2001;
                                                                      "Post" includes data from
                                                                      July 2001 to May 2005.
                                                                      The red line indicates the
                                                                      geometric mean above
                                                                      which the beneficial use is
                                                                      not achieved. There were
                                                                      significant reductions in
                                                                      mean levels of both £  coli
                                                                      and Enterococcus bacteria.
  Pre
                   Post
                                         Pre
                                                          Post
     U.S. Environmental Protection Agency
     Off ice of Water
     Washington, DC

     EPA841-F-07-001D
     April 2007
For additional information, contact:
Dan Butler
Oklahoma Conservation Commission
405-522-4500
dan.butler@conservation.ok.gov

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