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NCDA&CS
2017 Annual Progress Report
(Crop Year 2016) on the Neuse
Agricultural Rule
(15 A NCAC 2B.0238)
A Report to the Environmental Management Commission from the Neuse Basin
Oversight Committee: Crop Year 2016
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Summary
The Neuse Basin Oversight Committee (BOC) received and approved crop year (CY1) 2016
annual reports estimating the progress from the seventeen Local Advisory Committees (LACs)
operating under the Neuse Agriculture rule as part of the Neuse Basin Nutrient Management
Strategy. This report demonstrates agriculture’s ongoing collective compliance with the Neuse
Agriculture Rule and estimates further producer progress in decreasing nutrients. In CY2016,
agriculture collectively achieved an estimated 52% reduction in nitrogen loss from agricultural
lands compared to the 1991-1995 baseline, continuing to exceed the rule-mandated 30%
reduction. Sixteen of the seventeen LACs exceeded the 30% reduction goal established by the
BOC. The main reason for the greater nitrogen reduction in these counties is cropping shifts to
crops with lower nitrogen demands and application rates.
Rule Requirements and Compliance History
Effective December 1997, the rule provides
for a collective strategy for farmers to meet
the 30% nitrogen loss reductions within five
years. A BOC and seventeen LACs were
established to implement the Neuse
Agriculture rule and to assist farmers with
complying with the rule.
All seventeen Local Advisory Committees
(LACs) met as required in 2017. The LACs
submitted their first annual report to the BOC
in May 2002. That report estimated a
collective 38% reduction in nitrogen loss with
12 of the 17 LACs exceeding 30% individually.
In 2003, all LACs achieved their BOC
recommended reduction goal. All counties
are currently meeting their goal, with the
exception of Pamlico County, which reported
a 29% reduction. Division of Soil and Water
Conservation staff uses input from the LACs to calculate their annual reductions using the
Nitrogen Loss Estimation Worksheet (NLEW). Adjustments are made to reflect the most up-to-
date scientific research. These revisions lead to adjustments in both individual LAC and
basinwide nitrogen loss reduction rates.
1 The 2016 crop year began in October 2015 and ended in September 2016.
Neuse Nutrient Sensitive Waters (NSW)
Strategy
The Environmental Management Commission
(EMC) adopted the Neuse nutrient strategy in
December, 1997. The NSW strategy goal was
to reduce the average annual load of nitrogen
delivered to the Neuse River Estuary by 2003
from both point and non-point source
pollution by a minimum of 30% of the average
annual load from the baseline period (1991-
1995). Mandatory nutrient controls were
applied to address non-point source pollution
in agriculture, urban stormwater, nutrient
management, and riparian buffer protection.
The overall 30% nitrogen loading reduction
target for the Neuse River Estuary has not yet
been reached.
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Scope of Report and Methodology
The estimates provided in this report represent whole-county scale calculations of nitrogen loss
from cropland agriculture adjusted for acreage in the basin. These estimates were made by NC
Division of Soil and Water Conservation (DSWC) staff using the ‘aggregate’ version of the
Nitrogen Loss Estimation Worksheet, or NLEW, an accounting tool developed to meet the
specifications of the Neuse Rule and approved by the EMC. The development team included
interagency technical representatives of the NC Division of Water Resources (DWR), NC DSWC
and USDA-Natural Resources Conservation Service (NRCS) and was led by NC State University
Soil Science Department faculty. The NLEW captures application of both inorganic and animal
waste sources of fertilizer to cropland. It does not capture the effects of nitrogen applied to
pastureland and NLEW is an “edge-of-management unit” accounting tool; it estimates changes
in nitrogen loss from croplands, but does not estimate changes in nitrogen loading to surface
waters.
Annual Estimates of Nitrogen Loss and the Effect of NLEW Refinements
The NLEW software is periodically revised to incorporate new knowledge gained through
research and improvements to data. These changes have incorporated the best available data,
but changes to NLEW must be considered when comparing nitrogen loss reduction in different
versions of NLEW. Further updates in soil management units are expected as NRCS produces
updated electronic soils data. The small changes in soil management units are unlikely to
produce significant effects on nitrogen loss reductions. Figure 1 represents the annual percent
nitrogen loss reduction from the baseline for 2001 to 2016.
Figure 1. Collective Nitrogen Loss Reduction Percent 2001 to 2016 Based on NLEW, Neuse River
Basin.
0%
10%
20%
30%
40%
50%
60%
2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016Percent ReductionYear
NLEW v5.02 NLEW v5.31 NLEW v5.32 NLEW v5.33a NLEW v5.33b NLEW v6.0
30% Reduction Goal
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The first NLEW reports were run in 2001, and agriculture has continued to exceed its collective
30% nitrogen reduction goal since that time. The first NLEW revision (v5.31) marked a
significant decrease in the nitrogen reduction efficiencies of buffers based on the best available
research information, so baseline and CY2005 were re-calculated, and soil management units
were revised. The second (v5.32) and third (v5.33a) revisions were minor updates of soil
mapping units. In April of 2011 the NLEW Committee established further reductions (v5.33b) in
nitrogen removal efficiencies for buffers based on additional research. In 2016 NLEW software
was updated (v6.0) from outdated software and transferred to a web-based platform on
NCDA&CS servers. Revised realistic yield and nitrogen use efficiency data from NCSU was
incorporated, and some minor calculation errors were corrected for corn, sweet potatoes, and
sweet corn. Table 1 lists the changes in buffer nitrogen reduction efficiencies over time.
Table 1. Changes in Buffer Width Options and Nitrogen Reduction Efficiencies in NLEW
Buffer
Width
NLEW v5.02 % N Reduction
2001-2005
NLEW v5.31, v5.32, v5.33a
% N Reduction
2006-2010
NLEW v5.33b, v6.0
% N Reduction
2011-Current
20’ 40% (grass)*
75% (trees & shrubs)* 30% 20%
30' 65% 40% 25%
50' 85% 50% 30%
70' 85% 55% 30%
100' 85% 60% 35%
*NLEW v5.02 - the vegetation type (i.e. trees, shrubs, grass) within 20' and 50' buffers determined reduction values.
Based on research results, this distinction was dropped from subsequent NLEW versions.
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Current Status
Nitrogen Reduction from Baseline for CY2016
All seventeen LACs submitted their sixteenth annual reports to the BOC for approval in
September 2017. For the entire basin, in CY2016 agriculture achieved a 52% reduction in
nitrogen loss compared to the 1991-1995 baseline. This percentage is 1% lower than the
reduction reported for CY2015. Table 2 lists each county’s baseline, CY2015 and CY2016
nitrogen (lbs/yr) loss values, and nitrogen loss percent reductions from the baseline in CY2015
and CY2016.
Table 2. Estimated Reductions in Agricultural Nitrogen Loss from Baseline (1991-1995) for 2015
and 2016, Neuse River Basin*
County Baseline N
Loss (lb)
CY2015 N
Loss (lb)*
CY2015 N
Reduction (%)
CY2016 N
Loss (lb)*
CY2016 N
Reduction (%)
Carteret 1,292,586 654,572 49% 579,560 55%
Craven 4,153,187 1,574,823 62% 1,800,518 57%
Durham 220,309 39,312 82% 55,342 75%
Franklin 219,209 35,176 84% 33,896 85%
Granville 193,197 26,701 86% 64,180 67%
Greene 4,439,036 2,030,728 54% 2,083,290 53%
Johnston 6,728,638 3,162,882 53% 3,230,187 52%
Jones 3,283,906 1,859,200 43% 2,031,206 38%
Lenoir 4,455,752 2,711,731 39% 2,650,395 41%
Nash 1,042,072 392,916 62% 438,450 58%
Orange 787,040 109,040 86% 61,123 92%
Pamlico 2,023,294 1,551,263 23% 1,437,444 29%
Person 616,669 139,231 77% 80,349 87%
Pitt 3,399,455 1,604,914 53% 1,917,032 44%
Wake 1,434,602 347,179 76% 288,649 80%
Wayne 8,297,408 3,772,582 55% 3,493,873 58%
Wilson 3,273,647 1,729,865 47% 1,833,161 44%
Total 45,860,007 21,742,116 53% 22,078,655 52%
* Nitrogen loss values are for comparative purposes. They represent nitrogen that was applied to agricultural lands
in the basin and neither used by crops nor intercepted by BMPs in a Soil Management Unit, based on NLEW
calculations. This is not an in-stream loading value.
Nitrogen loss reductions were achieved through a combination of fertilization rate decreases,
cropping shifts, and BMP implementation. Winter weather during CY2016 was similar to that of
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CY2015, which means planted wheat acres remained low and reduction percentages fairly
stable. Factors that influence agricultural nitrogen reductions are shown in Table 3.
Pamlico County is working to improve their reduction, which increased this year compared to
CY2015. From CY2015 to CY2016 Pamlico experienced a decrease of 1,932 acres of wheat and
an increase of 1,540 acres of soybeans. The Pamlico Soil and Water Conservation District Board
is working to meet their reduction by making nutrient reducing BMPs a higher priority in their
annual NC Agriculture Cost Share Program (ACSP) strategy plan, and they installed water
control structures which achieve nutrient reductions on 400 acres in CY2016. In 2016 Pamlico
Soil and Water Conservation District was awarded a grant allocation to assist producers in
implementing water control structures, and these funds are currently being contracted. As of
CY2016 it is estimated that over 40% of agricultural land in Pamlico County currently has some
form of controlled drainage utilizing water control structures. The DSWC, LACs and additional
stakeholders are working with others in the agricultural community in this county and the
surrounding area to communicate the need for more BMP installation at existing commodity
outreach events. The BOC will continue to focus its efforts to monitor this county’s progress
and encourage BMP implementation.
The NLEW outputs and staff calculations estimate the factors that contributed to the nitrogen
reduction by the percentages shown in Table 3.
Table 3. Factors That Influence Nitrogen Reduction on Agricultural Lands (by percentage), Neuse
River Basin*
Practice CY2013
NLEW v5.33b
CY2014
NLEW v5.33b CY2015
NLEW v6.0
CY2016
NLEW v6.0
BMP implementation 7% 8% 9% 9%
Fertilization
management 6% 8% 10% 11%
Cropping shift 11% 18% 20% 18%
Cropland converted to
grass/trees 2% 2% 2% 2%
Cropland lost to idle land 4% 3% 4% 4%
Cropland lost to
development 7% 7% 8% 8%
Total 37% 46% 53% 52%
*Percentages are based on a total of the reduction, not a year-to-year comparison.
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BMP Implementation
As illustrated in Figure 2, CY2016 BMP implementation yielded a net increase of 435 acres
affected by water control structures and a net increase of 6,843 nutrient scavenger crop acres.
An accurate reassessment of active agricultural land and remaining buffer systems is badly
needed due to the rate at which urbanizing counties have lost agricultural land. A countywide
field analysis of buffer acres in Durham is currently being performed by SWCD staff, and they
plan to have a finalized report available in time for the CY2017 progress report. The findings of
this analysis will help inform subsequent efforts for other urbanized counties which have lost
agricultural acreages. An interim adjustment based on DEQ reports2 has led to a reduction of
20 ft. buffers by 755 acres, 30 ft. buffers by 683 acres, 50 ft. buffers by 2,122 acres, and 100 ft.
buffers by 4,015 acres. These adjusted totals have increased the accuracy of nitrogen loss
calculations.
BMP data is collected from state and federal cost share program active contracts, and in some
cases BMPs were installed without cost share funding. While there is some variability in the
data reported, LACs are reporting the best available information. As additional data is
collected, the LACs will review the sources and update their methodology for reporting if
warranted.
Every effort is being made to ensure that BMPs currently being reported continue to function
as designed. Verification of this functionality requires site visits to individual farm owners who
may or may not be under active contract. Coastal counties have reported that despite contract
expirations, the water control structures which have been checked and which are no longer
covered by an operation and maintenance agreement are still being actively managed by
producers.
Based on the comparison of total cropland acres and state or federal cost share program BMPs,
it is estimated that over a third of the Neuse River Basin’s cropland receives treatment from
reported nitrogen reducing BMPs. However, this treatment estimate does not take into
account the entire drainage area treated by buffers in the piedmont, which is generally 5 to 10
times higher than the actual acres of the buffer shown in Figure 2.3 Overall, the total acres of
implementation of BMPs have increased since the baseline, as illustrated in Figure 2. BMP
installation goals were set by the local nitrogen reduction strategy, which was approved by the
EMC in 1999. Agriculture exceeded all of these goals in CY2008.
2 Osmond, D.L., K. Neas. 2011. Delineating Agriculture in the Neuse River Basin. Prepared for NC Department of
Environment and Natural Resources (NCDENR), Division of Water Quality. http://content.ces.ncsu.edu/delineating-
agriculture-in-the-neuse-river-basin
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Figure 2: Cumulative Nitrogen Reducing BMPs Installed on Agricultural Lands for Baseline (1991-
1995) and from 2013-2016, Neuse River Basin (except for scavenger crops, which are an annual
practice)
The acres of buffers listed represent actual acres. Acres affected by the buffer could be 5 to 10 times larger in the piedmont than
the acreage shown above. 3
Additional Nutrient BMPs
Not all types of nutrient-reducing BMPs are tracked by NLEW. These include livestock-related
nitrogen and phosphorus reducing BMPs, BMPs that reduce soil and phosphorus loss, and BMPs
that do not have enough scientific research to support a nitrogen reduction benefit. The BOC
believes it is worthwhile to recognize these practices. Table 4 identifies BMPs not accounted for
in NLEW and tracks their implementation in the basin since CY1996.
Increased implementation numbers are evident in CY2016 across most BMP types. Some of
these BMPs will yield reductions in nitrogen loss that are not reflected in the NLEW accounting
in this report but will benefit the estuary.
Table 4: Nutrient-Reducing BMPs Not Accounted for in NLEW, 1996 to 2016, Neuse River Basin*
BMP Units 1996-2011 2013 2014 2015 2016
Diversion Feet 149,449 160,655 161,924 166,199 166,600
Fencing (USDA programs) Feet 154,885 170,501 204,869 214,748 228,216
Field Border Acres 3,337 5,211 5,217 5,219 5,225
Grassed Waterway Acres 2,261 2,300 2,351 2,358 2,377
Livestock Exclusion Feet 81,389 100,860 103,121 118,178 125,190
Precision Agriculture Acres 0 2,567 3,567 3,660 3,664
Sod Based Rotation Acres 60,115 92,404 92,404 101,429 102,752
Tillage Management Acres 34,072 48,649 53,634 59,057 59,680
Terraces Feet 49,970 50,670 50,670 76,175 76,175
3 Bruton, Jeffrey Griffin. 2004. Headwater Catchments: Estimating Surface Drainage Extent Across North Carolina and Correlations Between
Landuse, Near Stream, and Water Quality Indicators in the Piedmont Physiographic Region. Ph.D. Dissertation. Department of Forestry and
Environmental Resources, North Carolina State University, Raleigh, NC 27606. http://www.lib.ncsu.edu/theses/available/etd-03282004-
174056/
0
20,000
40,000
60,000
80,000
100,000
120,000
Scavenger
Crop
20' Buffer 30' Buffer 50' Buffer 100' Buffer Water Control
StructureAcresBMP
Baseline 2013 2014 2015 2016
*Cumulative data provided using active contracts in State and Federal cost share programs.
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Fertilization Management
Better nutrient management has resulted in
farmers in the Neuse River Basin reducing their
fertilizer application from baseline levels.
Despite annual fluctuations, fertilization rates
for all major crops in the basin have been
reduced from the baseline period.
Between CY2015 and CY2016 nitrogen
application rates increased by 9 lbs per acre on
bermuda hay and 2 lbs per acre on fescue hay,
while all other nitrogen application rates
remained stable. Figure 3 shows these
corresponding application rates.
Due to lower commodity prices, there has been
an economic incentive for producers to
consider more efficient nitrogen rates, timing, and placement alternatives. Fertilizer rates and
standard application practices are revisited annually by LACs using data from farmers,
commercial applicators and state and federal agencies’ professional estimates.
Figure 3. Average Annual Nitrogen Fertilization Rate (lbs/ac) for Agricultural Crops for the
baseline (1991-1995) and 2013-2016, Neuse River Basin
0
50
100
150
200
250
300
Bermuda Corn Cotton Fescue Soybeans Tobacco WheatNitrogen Rate lbs/ acreCrops
Baseline 2013 2014 2015 2016
Factors Identified by LACs Contributing to
Reduced Nitrogen Application Rates
➢ Economic decisions and fluctuating
farm incomes.
➢ Increased education and outreach on
nutrient management (NC Cooperative
Extension held 21 nutrient
management training sessions,
approximately 2,000 farmers and
applicators received training.)
➢ Mandatory animal waste management
plans
➢ The federal government tobacco quota
buy-out reducing tobacco acreage.
➢ Neuse and Tar-Pamlico Nutrient
Strategies
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Cropping Shifts
The LACs recalculate the cropland acreage annually by utilizing crop data reported by farmers
to the Farm Service Agency. Because each crop type requires different amounts of nitrogen and
utilizes applied nitrogen with a different efficiency rate, changes in the mix of crops grown can
have significant impact on the cumulative yearly nitrogen loss reduction. The BOC anticipates
that the basin will see additional crop shifts in the upcoming year based on changing
commodity prices and wet weather.
Corn requires higher nitrogen application rates than other crops, and corn acres increased by
over 45,400 acres from CY2015 to CY2016 due to a temporary price increase. Cotton prices
remained low, so cotton decreased by over 17,000 acres from CY2015 to CY2016. Soybean
acres, which require no nitrogen input, saw a decrease of over 32,500 acres between CY2015
and CY2016, and this transition caused a slight increase in overall nitrogen loss. In addition, a
second consecutive extremely wet fall prevented many farmers from accessing their fields in
time to plant a crop of winter wheat. In most cases wheat acres are “double cropped” with
soybeans, which means that wheat acres are planted on the same acreage before a spring
soybean crop. In CY2016, soybean acreages were accounted for in these double cropped
systems, but some of those acres were not fertilized over the winter months where a wheat
crop was not planted. This resulted in an overall decrease of over 47,800 wheat acres between
CY2015 and CY2016. A host of factors from individual to global determine crop choices.
Figure 4. Acreage of Major Crops for the Baseline (1991-1995) and 2013-2016, Neuse River
Basin
0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
400,000
Hay Corn Cotton Soybeans Tobacco WheatAcres
Crops
Baseline 2013 2014 2015 2016
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Land Use Change to Development, Idle Land and Cropland Conversion
The number of cropland acres will fluctuate every year in the Neuse River Basin. Each year,
some cropland is permanently lost to development or converted to grass or trees. However,
idle land is agricultural land that is currently out of production but could be brought back into
production at any time. Cropland conversion and cropland lost to development is land taken
out of agricultural production and is unlikely to be returned to production. As of 2015 it was
estimated that more than 81,000 acres have been lost to development, and currently more
than 22,109 acres have been converted to grass or trees since the baseline. For CY2016 there
are approximately 45,355 idle acres and a total of 714,302 NLEW-accountable crop acres.
These estimates come from the LAC members’ best professional judgment, USDA-Farm Service
Agency (FSA) records and county planning departments. The total crop acres are obtained from
USDA-FSA and NC Agricultural Statistics annual reports. Cropland acres have continued to
decrease from the baseline period, and CY2016 experienced a reduction of over 51,596 crop
acres from CY2015 (see Figure 5). A significant portion of this acreage reduction was due to the
reduction in wheat, some of which would have been planted but for wet weather.
Figure 5. Total NLEW Accounted Crop Acres in the Neuse River Basin, Baseline (1991-1995) and
2001-2016.
0
200000
400000
600000
800000
1000000
1200000
Baseline 2002 2004 2006 2008 2010 2012 2014 2016Acres
Year
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Looking Forward
The Neuse BOC will continue to report on rule implementation, relying heavily on Soil and
Water Conservation District staff to compile crop reports. The BOC continues to encourage
counties to implement additional BMPs to further reduce nitrogen loss.
Because cropping shifts are susceptible to
various pressures, the BOC is working with
LACs in all counties to continue BMP
implementation that provides for a lasting
reduction in nitrogen loss in the basin while
monitoring cropping changes. Due to
improved weather during the fall growing
season in late 2016, the BOC expects
reported wheat acre totals in CY2017 to
increase significantly.
The Neuse BOC will continue to monitor
and evaluate crop trends. The current shift
to and from crops with higher nitrogen
requirements may continue to influence
the yearly reduction. Additionally,
members of the BOC plan to participate in
a land accounting work group, if
reconvened, with the Division of Water
Resources to assist in developing a more consistent land accounting framework.
Funding
Ongoing agriculture rule reporting has incorporated data processing efficiencies and
improvements in recent years. NLEW upgrades have allowed LAC members to more actively
participate in the compilation of data and analysis of nitrogen loss trends, and a new Division of
Soil and Water Conservation contracting system has helped optimize BMP documentation
efforts. Each year it is estimated that 150 LAC members spend over 225 hours on agriculture
rule reporting, which accumulates to over $5,400 worth of volunteer time. The Division of Soil
and Water Conservation, funded through an EPA 319(h) grant, expends approximately $50,000
on agricultural reporting staff support annually.
In CY2016 soil and water conservation districts spent over $887,000 through the Agriculture
Cost Share Program in the Neuse River Basin, and the Natural Resources Conservation Service
spent over $3,676,754 through the Environmental Quality Assistance Program in the counties of
the Neuse and Tar-Pamlico River Basins. The EPA 319(h) grant program, which is administered
by the Department of Environmental Quality, has approximately $1.2 million in competitive
grant funds available for implementation of approved nonpoint source management programs.
Grant funds from the 319(h) program can be used to supplement technical assistance, match
Basin Oversight Committee recognizes the
dynamic nature of agricultural business.
➢ Changes in world economies, energy or
trade policies.
➢ Changes in government programs (i.e.,
commodity support or environmental
regulations)
➢ Weather (i.e., long periods of drought or
rain)
➢ Scientific advances in agronomics (i.e.,
production of new types of crops or
improvements in crop performance)
➢ Plant disease or pest problems (i.e.,
viruses or foreign pests)
➢ Urban encroachment (i.e., crop selection
shifts as fields become smaller)
➢ Age of farmer (i.e, as retirement
approaches farmers may move from row
crops to cattle)
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cost share funding, and support BMP implementation. These programs have all helped fund
erosion and nutrient reducing best management practices in the Neuse Basin. Participation by
so many members of the local agricultural community demonstrates a commitment toward
achieving the nutrient strategy’s long-term goals.
Farmers and agency staff personnel with other responsibilities serve on the LACs in a voluntary
capacity. With less funding available for reporting support at the state level, responsibility for
compilation of annual local progress reports falls on these LACs and Soil and Water
Conservation District staffs. Few currently serving LAC members were active during the
stakeholder process for the Agriculture Rule, so some institutional knowledge about annual
reporting requirements has been lost. As a result, training of new Soil and Water Conservation
District staff and LAC members regarding rule requirements and reporting is ongoing.
Funding is an integral part in the success of reaching and maintaining the goal through technical
assistance and BMP implementation. It is also important for data collection and reporting.
At the present time there is also no funding for a basin coordinator. Part of the responsibilities
of the technicians and basin coordinators was to assist with the reporting requirements for the
Neuse and Tar-Pamlico Agriculture Rules. In addition to his other duties, an employee within
the NCSA&CS Division of Soil and Water Conservation has been assigned the data collection,
compilation and reporting duties for the Agriculture Rules for all existing Nutrient Sensitive
Waters Strategies.
Now that watershed technician funding has been eliminated, a more centralized approach to
data collection and verification is necessary. This evolving approach will involve GIS analysis
and more streamlined FSA acreage documentation. Durham County, for example, has hired
part-time staff to assist with detailed agricultural land delineation, including field verification of
intact best management practices. Results of this analysis should be available for the CY2017
annual report. Few counties have these kinds of resources, however, so LACs will be trained to
handle the new workload to the best of their ability. Because most district staffs have neither
the time nor financial resources to synthesize county level data, this centralized collection
approach will come at the expense of local knowledge. Annual agricultural reporting is required
by the rules; therefore, continued funding for the Division’s only remaining nutrient coordinator
position is essential for compliance.
Previously, funding was available for research on conservation practice effectiveness, realistic
yields, and nitrogen use efficiencies. Due to eligibility changes and other funding constraints, it
is unlikely that new data will be developed. Prior funding sources for such research, which
provided much of the scientific information on which NLEW was based, are no longer available.
Should new funding be made available, additional North Carolina-specific research information
could be incorporated into future NLEW updates.
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Conclusion
Significant progress has been made in agricultural nitrogen loss reduction, and the agricultural
community consistently reaches its 30% reduction goal. However, the measurable effects of
these BMPs on overall in-stream nitrogen reduction may take years to develop due to the
nature of non-point source pollution. Nitrogen reduction values presented in this annual
summary of agricultural reductions reflect “edge-of-management unit” calculations that
contribute to achieving the overall 30% nitrogen loss reduction goal. Significant quantities of
agricultural BMPs have been installed since the adoption and implementation of the nutrient
management strategy, and agriculture continues to do its part towards achieving the overall
goal of a 30% reduction of nitrogen delivered to the Neuse estuary.