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Conservation Work Leads to Atrazine Delisting of Shell „reek
Waterbody Irnproved High levels of agricultural runoff led to Shell Creek being listed
as impaired for atrazine on the Nebraska state Clean Water Act
section 303(d) list of impaired waters in 2006. Prior to this listing, in 1999, a group of landowners
formed the Shell Creek Watershed Improvement Group (SCWIG) to address chronic flooding, poor
water quality, poor fishery and instability of Shell Creek, With the help of conservation agencies,
they developed and implemented a watershed management plan (2005-2015) to resolve these
issues. A decade of dedicated conservation work in the watershed significantly reduced the number
of exceedances of the aquatic life standard for atrazine, allowing one segment of Shell Creek, LP1-
20700, to be delisted in 2018 for aquatic life impairment due to atrazine.
Problem
Shell Creek is a 110-miie-iong stream in northeastern
Nebraska flowing into the Platte River near the city
of Schuyler. It drains a 304,897-acre watershed
dominated by row crop production (primarily corn
and soybeans) and pastureland. The main channel is
composed of four segments: LP1-20600, LP1-20700,
L.P1-20800 and L12-20900 (Figure 1).
Very low levels of conservation practices on croplands
in the watershed led to high runoff rates and elevated
levels of atrazine in Shell Creek. Numerous exceed-
ances of the aquatic life standard for atrazine (12
micrograms per liter [|ig/L]) prompted the Nebraska
Department of Environmental Quality (NDEQ) to list
Shell Creek stream segment LP1-20700 as impaired for
aquatic life use due to atrazine in 2006.
Story Highlights
A series of projects conducted under the Shell Creek
Watershed Management Plan incorporated traditional
cropland treatment and near and in-stream treat-
ments to abate atrazine contamination within the Shell
Creek watershed and enhance aquatic life habitat. The
project also reduced runoff of nitrogen, phosphorus
and sediment. The watershed was divided into 10
subwatersheds for implementation of conservation
practices. Cost share for conservation practices was
offered in the subwatersheds for 2 years on a rota-
tional basis until the entire watershed was covered.
Lands within a 3,000-foot corridor along the stream
channel were continuously eligible for cost share.
The Natural Resources Conservation Service (NRCS)
extended dedicated Environmental Quality Incentives
Program (EQIP) funding through the Nebraska State
Water Quality Initiative. Participants in cost share
programs for agricultural practices were determined
through a screening tool designed to target the most
effective best management practices (BMPs) for
atrazine management in priority subwatersheds and
the stream corridor. Priority practices for cropland
included crop rotation, integrated pest management,
water and sediment control basins, no till, grass water-
ways, cover crops, riparian buffers and filter strips.
Stream stabilization practices were prioritized to
protect public infrastructure such as roads, bridges
and utility lines. Priority practices included streambank
stabilization, floodplain benches, aquatic habitat
enhancement, riparian buffers and filter strips.

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Septic system upgrades and well decommissioning
were eligible for cost share in the watershed, but
preference was given to applications within priority
areas. These were considered special priority practices
designed to address a specific local issue and to directly
engage property owners in promoting the project.
SCWIG and partner agencies worked with operators
and landowners to help them enroll in conservation
programs and implement BMPs. Information and
education on nonpoint source pollution manage-
ment was disseminated through meetings, tours and
demonstrations. Volunteer stream monitoring by area
schools continues to engage students and the public in
learning about and responding to water quality issues.
Many BMPs were implemented through Shell Creek
watershed projects, including no till (8,043 acres [ac]),
no-till consultant (3,132 ac), nutrient management
(841 ac), non-invasive nitrogen application (2,749 ac),
contour buffer (17 ac), habitat buffer (97 ac), field
windbreak (6 ac), filter strip (175 ac), grassed waterway
(45 ac), riparian buffer (6 ac), cover crop (2,571 ac),
pond (1), sediment basins (75), wastewater treatment
system inspections (7) and upgrades (88), and well
decommissioning (58).
Nebraska Educational Television produced a segment
featuring the Newman Grove Student's volunteer
monitoring program as part of its series, I Love Public
Schools. In addition, NDEQ, Nebraska Extension, and
NRCS produced a 90-second video featuring the Shell
Creek project for the Environmental Council of States
(ECOS). The ECOS video was used for presentations.
Results
The number of exceedances of the atrazine aquatic
life standard declined after implementation of the
Shell Creek Watershed Management Plan began in
2005 (Figure 2). Out of 48 water samples collected
from Shell Creek between 2007 and 2016, only seven
samples out of a permissible eight samples exceeded
the water quality standard of 12 |ig/L atrazine. As a
result, Shell Creek segment LPl-20700was delisted for
atrazine impairment in 2018. In addition, phosphorous
loads decreased by 9,788 pounds (lbs) per year (yr),
nitrogen loads decreased by 36,455 Ibs/yr and sedi-
ment loads decreased by 6,398 tons/yr.
Shell Creek Atrazine Concentrations (fjg/LJ
•



.






—Aquatic life chronic water quality











•Trend line of atrazine concentrations
(ug/L) on Shell Creek




























































i.OO l-«—I	1	1	1	Mt—I ¦ |	1-8—J-»—1-# I m—I / I % I • I 0 I	| »—|
\ % % % % % % % % % % % % % % % % % % %> %
\ % % % % % % % °> \ % % % % % % % % °<> % %
Sample Date
Figure 2. Atrazine concentrations declined after project
implementation began in 2005.
Implementing the first management plan yielded
significant progress in getting effective management
practices implemented on agricultural lands through-
out the watershed. For example, the use of no till
applied to cropland increased from approximately 14%
to 67% over the life of the first management plan.
Partners and Funding
Lower Platte North Natural Resources District admin-
istered external grants and coordinated selection and
implementation of conservation practices among
available programs. The District also provided funding
and technical assistance to install BMPs ($194,330).
Landowners contributed $471,822 toward practices.
SCWIG provided leadership in contacting producers
and landowners and encouraging their participation in
conservation programs and project activities. SCWIG
organized watershed outreach activities and advised
partner agencies on opportunities to work with
interested stakeholders.
NRCS provided funding and technical assistance
through EQIP ($1,121,359) and other U.S. Department
of Agriculture programs. Nebraska Environmental Trust
provided funding for installation of BMPs ($1,310,000).
NDEQ (now the Nebraska Department of Environment
and Energy) provided funding and technical assistance
through the CWA Section 319 Program ($658,280).
^£DSrX
PRO^°
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U.S. Environmental Protection Agency
Office of Water
Washington, DC
EPA 841-F-20-001PP
December 2020
For additional information contact:
Tom Mountford
Lower Platte North Natural Resources District
402-443-4665 • tmountford@lpnnrd.org
Elbert Traylor
Nebraska Department of Environment and Energy
402-471-2585 • Elbert.Traylor@nebraska.gov

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