490006_Application - 07 NMP soiltest_20240326

Required Soil Test Values
Rocky Creek Dairy
The Required Soil Test Values shown in the following table provide a summary of recommended actions that
should be taken based off information provided at time of soil tests. Fields that receive manure must have a soil
analysis conducted at least once every three years. High levels of zinc and copper can adversely affect plant
growth. Alternative crop sites must be used when the concentration of these metals approach excessive levels.
Site life can be estimated by dividing the amount of copper and zinc to be applied in Ibs/acre by 0.036 and 0.071,
respectively and multiplying the result by 0.85. By adding this quantity to the current soil index for copper or zinc,
we can predict life of the site for waste disposal.
In addition to copper and zinc indices, this table also provides a summary of lime recommendations for each
crop based on the first crop listed on the most recent soil sample. Application of lime at recommended rates is
necessary to maintain soil pH in the optimum range for crop production. If the first crop or rotation changes,
these recommendations may need to be reevaluated to ensure optimal ranges ofr crop production are
maintained.
Tract ID
Field ID
Crop(s)
pH
Lime Recom.
for Crop(s)
(tons/acre)
Cu4
Copper
Recommendation
Zn-1
Zinc
Recommendation
3835
1
Corn silage, SG/Corn silage
6.8
0,0
255
0,0
473
0,0
3835
2
Corn silage, SG/Corn silage
6.8
0,0
255
0,0
473
0,0
3835
3
Corn silage, SG/Corn silage
6.8
0,0
255
0,0
473
0,0
3835
4
Corn silage, SG/Corn silage
6.8
0,0
255
0,0
473
0,0
3850
1
Corn silage, SG/Corn silage
5.7
0.4, 0
90
0,0
218
j 0,0
3850
2
Corn silage, SG/Corn silage
5.7
0.4, 0
90
0,0
218
0,0
3864
1
Corn silage, SG/Corn silage
6.5
0,0
196
0,0
631
0,0
3864
2
Corn silage, SG/Com silage
6.5
0,0
196
0,0
631
0,0
3864
3
Corn silage, SG/Com silage
6.5
0,0
196
0,0
631
0,0
3864
4
Corn silage, SG/Corn silage
6.5
0,0
196
0,0
631
0,0
3865
1
Corn silage, SG/Corn silage
6.1
0,0
66
0,0
295
0,0
3873
1
Corn silage, SG/Corn silage
5.8
0.5, 0
253
0,0
294
0,0
3879
1
Corn silage, SG/Corn silage
5.8
0.5, 0
253
0,0
294
0,0
3879
2
Corn silage, SG/Corn silage
5.8
0.5, 0
253
0,0
294
0,0
3879
3
Corn silage, SG/Corn silage
5.8
0.5, 0
253
0,0
294
0,0
3884
1
Corn silage, SG/Corn silage
5.7
0.5, 0
263
0,0
251
0,0
3899
1
Corn silage, SG/Corn silage
6.5
0,0
88
0,0
98
0,0
3899
2
Corn silage, SG/Corn silage
6.5
0,0
88
0,0
98
0,0
3899
3
Corn silage, SG/Corn silage
6.5
0,0
88
0,0
98
0,0
3899
4
Corn silage, SG/Corn silage
6.5
0,0
88
0,0
98
0,0
3940
1
Corn silage, SG/Corn silage
5.7
0.5, 0
263
0,0
251
0,0
3/19/2024 5:45:19 PM 1 / 4

Required Soil Test Values
Rocky Creek Dairy
3956
1
Corn silage, SG/Com silage
6.3
0,0
176
0,0
144
0,0
3956
2
Corn silage, SG/Com silage
6.3
0,0
176
0, 0
144
0,0
3987
1
Corn silage, SG/Com silage
6.8
0,0
100
0,0
120
0,0
3987
2
Corn silage, SG/Com silage
6.8
0,0
100
0,0
120
0,0
3991
1
Corn silage, SG/Corn silage
6.3
0,0
165
0, 0
238
0, 0
5518_544
5
1
0
0, 0
0
0,0
0
0, 0
5518_544
5
2
0
0, 0
0
0, o
0
0, 0
5728
1
6.5
0,0
238
0,0
490
0, 0
5728
2
6.5
0,0
238
0,0
490
0,0
5729
1
Corn silage, SG/Corn silage
6.2
0, 0
65
0, 0
316
0,0
5729
2
Corn silage, SG/Corn silage
6.2
0, 0
65
0, 0
316
0, 0
5729
3
Corn silage, SG/Corn silage
6.2
0,0
65
0, 0
316
0, 0
8307
1
Corn silage, SG/Corn silage
6.4
0,0
183
0,0
244
0,0
8307
2
Corn silage, SG/Corn silage
6.4
0, 0
183
010
244
0,0
8720
1
Corn silage, SG/Corn silage
6.4
0,0
67
0,0
320
0,0
9314
1
Corn silage, SG/Com silage
6.7
0,0
211
0,0
537
0,0
9314
2
Corn silage, SG/Corn silage
6.7
0, 0
211
j 0,0
537
0,0
9451
1
Corn silage, SG/Corn silage
7.1
0, 0
2054
C, C
1011
0, 0
9451
2
Corn silage, SG/Corn silage
7.1
0,0
2054
C, C
1011
0, 0
9451
3
Corn silage, SG/Corn silage
7.1
0,0
2054
C, C
1011
0,0
9451
4
Corn silage, SG/Corn silage
7.1
0,0
2054
C, C
1011
0,0
9451
5
Corn silage, SG/Corn silage
7.1
0,0
2054
C, C
1011
0,0
9451
6
Corn silage, SG/Com silage
7.1
0, 0
2054
C, C
1011
0, 0
9451
7
Corn silage, SG/Corn silage
7.1
0, 0
2054
C, C
1011
0, 0
9451
8
Corn silage, SG/Corn silage
7.1
0,0
2054
C, C
1011
0,0
9451
9
Corn silage, SG/Corn silage
7.1
0, 0
2054
C, C
1011
0, 0
9451
10
Corn silage, SG/Com silage
7.1
0,0
2054
C, C
1011
0,0
9452
1
Corn silage, SG/Com silage
6.2
0,0
173
0,0
147
0,0
9452
2
Corn silage, SG/Corn silage
6.2
0,0
173
0, 0
147
0, 0
9452
3
Corn silage, SG/Com silage
6.2
0, o
173
0, 0
147
0, o
9452
4
Corn silage, SG/Com silage
6.2
0, o
173
0,0
147
0, o
3/19/2024 5:45:19 PM 2 / 4

Required Soil Test Values
Rocky Creek Dairy
9961
1
Corn silage, SG/Com silage
7.3
0,0
206
0,0
384
0,0
9961
2
Corn silage, SG/Com silage
7.3
0,0
206
0, 0
384
0,0
9961
3
Corn silage, SG/Com silage
7.3
0,0
206
0,0
384
0,0
9961
4
Com silage, SG/Com silage
7.3
0, 0
206
0,0
384
0,0
9961
5
Corn silage, SGICorn silage
7.3
0,0
206
0,0
384
0,0
9961
6
Corn silage, SGICom silage
7.3
0,0
206
0, 0
384
0,0
9961
7
Corn silage, SG/Corn silage
7.3
0, 0
206
0,0
384
0,0
9961
8
Corn silage, SG/Corn silage
7.3
0,0
206
0,0
384
0,0
9961
9
Corn silage, SG/Corn silage
7.3
0,0
206
0,0
384
0,0
9961
10
Corn silage, SG/Com silage
7.3
0,0
206
0,0
384
0,0
10159
1
7
0,0
48
0,0
118
0,0
10438
1
Corn silage, SG/Corn silage
6.8
0,0
519
0,0
328
0,0
10438
2
Corn silage, SG/Corn silage
6.8
0,0
519
0,0
328
0,0
10438
3
Corn silage, SG/Corn silage
5.9
0,0
229
0,0
175
0,0
10439
1
Corn silage, SG/Com silage
6
0,0
213
0,0
190
0,0
10682
1
Corn silage, SG/Corn silage
6.2
0,0
108
0,0
61
0, 0
10682
2
Corn silage, SG/Corn silage
6.2
0,0
108
0,0
61
0,0
10682
3
Corn silage, SG/Corn silage
6.2
0,0
108
0,0
61
0,0
10682
4
Corn silage, SG/Corn silage
6.2
0,0
108
0,0
61
0,0
10682
5
Corn silage, SGICom silage
6.2
0,0
108
0,0
61
0,0
10941_92
14
1
Corn silage, SGICom silage
6.2
0,0
108
0,0
61
0,0
40000
1
Corn silage, SGICorn silage
6.7
0, 0
105
0, 0
69
0,0
50000
1
Corn silage, SG/Com silage
6.4
0,0
130
0,0
93
0,0
70000
1
6.8
0,0
65
0,0
50
0,0
80000
1
Corn silage, SGICorn silage
5.5
0.5, 0
57
0, 0
128
0,0
90000
1
7
0,0
48
0, 0
118
0,0
92000
1
Corn silage, SG/Corn silage
5.7
0.4, 0
90
0,0
218
0,0
92000
2
Corn silage, SGICorn silage
5.7
0.4, 0
90
0,0
218
0,0
93000
1
6.9
0,0
53
0,0
123
0,0
3/19/2024 5:45:19 PM 3 / 4

Required Soil Test Values
Rocky Creek Dairy
Zinc and Copper Toxicity Levels in Soils
Metal
Soil Test Index
Recommended Action
Zn
300
Limit application on peanuts. Maintain soil pH >= 6.0.
500
Cease application on peanut land. Maintain soil pH >= 6.0.
2000
Caution: seek alternative site (all crops). Maintain soil pH >= 6.0.
3000
Cease application (all crops). Maintain soil pH — 6.0.
Cu
2000
Caution: seek alternative site (all crops). Maintain soil pH >= 6.0.
3000
Cease application (all crops). Maintain soil pH >= 6.0.
3/19/2024 5:45:19 PM 4 / 4

Required Specifications For Animal Waste Management
1. Animal waste shall not reach surface waters of the state by runoff, drift,
manmade conveyances, direct application, or direct discharge during
operation or land application. Any discharge of waste that reaches surface
water is prohibited.
2. There must be documentation in the design folder that the producer either
owns or has an agreement for use of adequate land on which to properly
apply the waste. If the producer does not own adequate land to properly
dispose of the waste, he/she shall provide evidence of an agreement with a
landowner, who is within a reasonable proximity, allowing him/her the use of
the land for waste application. It is the responsibility of the owner of the
waste production facility to secure an update of the Nutrient Management
Plan when there is a change in the operation, increase in the number of
animals, method of application, receiving crop type, or available land.
3. Animal waste shall be applied to meet, but not exceed, the nitrogen needs
for realistic crop yields based upon soil type, available moisture, storical data,
climatic conditions, and level of management, unless there are regulations
that restrict the rate of applications for other nutrients.
4. Animal waste shall be applied to land eroding less than 5 tons per acre per
year. Waste may be applied to land eroding at more than 5 tons per acre per
year but less than 10 tons per acre per year provided grass filter strips are
installed where runoff leaves the field (see USDA, NRCS Field Office Technical
Guide Standard 393 - Filter Strips).
s. Odors can be reduced by injecting the waste or by disking after waste
application. Waste should not be applied when there is danger of drift from
the land application field.

6. When animal waste is to be applied on acres subject to flooding, waste will
be soil incorporated on conventionally tilled cropland. When waste is applied
to conservation tilled crops or grassland, the waste may be broadcast
provided the application does not occur during a season prone to flooding
(see "Weather and Climate in North Carolina" for guidance).
7. Liquid waste shall be applied at rates not to exceed the soil infiltration rate
such that runoff does not occur offsite or to surface waters and in a method
which does not cause drift from the site during application. No ponding
should occur in order to control odor and flies.
s. Animal waste shall not be applied to saturated soils, during rainfall events, or
when the soil surface is frozen.
9. Animal waste shall be applied on actively growing crops in such a manner
that the crop is not covered with waste to a depth that would inhibit growth.
The potential for salt damage from animal waste should also be considered.
Zo. Nutrients from waste shall not be applied in fall or winter for spring planted
crops on soils with a high potential for leaching. Waste/nutrient loading rates
on these soils should be held to a minimum and a suitable winter cover crop
planted to take up released nutrients. Waste shall not be applied more than
30 days prior to planting of the crop or forages breaking dormancy.
11. Any new swine facility sited on or after October 1, 1995 shall comply with the
following: The outer perimeter of the land area onto which waste is applied
from a lagoon that is a component of a swine farm shall be at least 50 feet
from any residential property boundary and canal. Animal waste, other than
swine waste from facilities sited on or after October 1, 1995, shall not be
applied closer than 25 feet to perennial waters.
12. Animal waste shall not be applied closer than 100 feet

13. Animal waste shall not be applied closer than 200 feet of dwellings other
than those owned by the landowner.
14. Waste shall be applied in a manner not to reach other property and public
right-of-ways.
1s. Animal waste shall not be discharged into surface waters, drainage ways, or
wetlands by a discharge or by over -spraying. Animal waste may be applied
to prior converted cropland provided the fields have been approved as a land
application site by a "technical specialist". Animal waste shall not be applied
on grassed waterways that discharge directly into water courses, and on
other grassed waterways, waste shall be applied at agronomic rates in a
manner that causes no runoff or drift from the site.
16. Domestic and industrial waste from wash down facilities, showers, toilets,
sinks, etc., shall not be discharged into the animal waste management
system.
17. A protective cover of appropriate vegetation will be established on all
disturbed areas (lagoon embankments, berms, pipe runs, etc.). Areas shall
be fenced, as necessary, to protect the vegetation. Vegetation such as trees,
shrubs, and other woody species, etc., are limited to areas where considered
appropriate. Lagoon areas should be kept mowed and accessible. Berms
and structures should be inspected regularly for evidence of erosion,
leakage, or discharge.
18. If animal production at the facility is to be suspended or terminated, the
owner is responsible for obtaining and implementing a "closure plan" which
will eliminate the possibility of an illegal discharge, pollution, and erosion.
19. Waste handling structures, piping, pumps, reels, etc., should be inspected on
a regular basis to prevent breakdowns, leaks, and spills. A regular
maintenance checklist should be kept on site.

2o. Animal waste can be used in a rotation that includes vegetables and other
crops for direct human consumption. However, if animal waste is used on
crops for direct human consumption, it should only be applied pre -plant with
no further applications of animal waste during the crop season.
21. Highly visible markers shall be installed to mark the top and bottom
elevations of the temporary storage (pumping volume) of all waste
treatment lagoons. Pumping shall be managed to maintain the liquid level
between the markers. A marker will be required to mark the maximum
storage volume for waste storage ponds.
22. Waste shall be tested within 60 days of utilization and soil shall be tested at
least annually at crop sites where waste products are applied. Nitrogen shall
be the rate -determining nutrient, unless other restrictions require waste to
be applied based on other nutrients, resulting in a lower application rate
than a nitrogen based rate. Zinc and copper levels in the soils shall be
monitored and alternative crop sites shall be used when these metals
approach excessive levels. pH shall be adjusted and maintained for optimum
crop production. Soil and waste analysis records shall be kept for a minimum
of five years. Poultry dry waste application records shall be maintained for a
minimum of three years. Waste application records for all other waste shall
be maintained for five (5) years.
23. Dead animals will be disposed of in a manner that meets North Carolina
regulations.

USDA United States NUTRIENT MANAGEMENT PLAN
Department of
Agriculture SUPPLEMENTAL INFORMATION
Implementation Requirements (590)
Prepared for: Rocky Creek Dairy, Ben Shelton
Prepared by: Sam Bingham, Engineer
Farm:
WHAT IS NUTRIENT MANAGEMENT?
Nutrient Management is applying nutrients from all
sources with the right placement, in the right
amount, at the right time, and from the right source
to minimize nutrient losses to surface and
groundwater. This practice is accomplished
through development and implementation of a
Nutrient Management Plan, which can be part of a
broader Conservation Plan or CNMP that
addresses multiple resource concerns.
PURPOSE OF NUTRIENT MANAGEMENT
A nutrient management plan is intended to
accomplish one or more of the following objectives:
• To budget, supply, and conserve nutrients for
plant production.
• To minimize agricultural nonpoint source
pollution of surface and groundwater
resources.
• To properly utilize manure or organic by-
products as a plant nutrient source.
• To protect air quality by reducing odors,
nitrogen emissions (ammonia, oxides of
nitrogen), and the formation of atmospheric
particulates.
• To maintain or improve the physical, chemical,
and biological condition of soil.
CONTENTS OF THE NUTRIENT
MANAGEMENT PLAN
For NC DENR-DWR or NPDES permitted animal
operations, the plan and specifications must
include all elements required by the Certified
Animal Waste Management Plan and Permit.
Tract: See Maps in Plan Date: 3/2024
The following components are included in the
nutrient management plan for the planned
application site:
• aerial site photograph(s)/imagery or site
map(s), and a soil survey map of the site,
• Sufficient soils information —such as dominant
soil map until for each planned field —needed
to apply nutrients at RYE and Soil Test Report
determined rates as appropriate; and to not
exceed rates determined by nutrient risk
assessment planning criteria.
• location of designated sensitive areas and the
associated nutrient application restrictions and
setbacks,
• results of approved risk assessment tools for
nitrogen, phosphorus, and erosion losses. In
NC, the most recent PLAT results are a
required part of the nutrient management plan.
• current and/or planned plant production
sequence or rotation,
• soil, water, compost, manure, organic by-
product, and plant tissue sample analyses
applicable to the plan,
• realistic yield goals for the crops,
• complete nutrient budget for nitrogen,
phosphorus, and potassium for the plant
production sequence or crop rotation,
• listing and quantification of all nutrient sources
and form,
• in accordance with the nitrogen and
phosphorus risk assessment tool(s), specify
the recommended nutrient application source,
timing, amount (except for precision/variable
rate applications specify method used to
determine rate), and placement of plant
nutrients for each field or management unit,
and
Implementation Requirements- North Carolina NRCS
Nutrient Management (590) Page 1 of 5 August 2019

• guidance for implementation, operation and
maintenance, and recordkeeping as specified
by the CNMP or applicable NC DWQ or
NDPES permit.
Also, where precision/variable rate nutrient
application applications are made, the following
components are required in nutrient management
planning:
• The geo-referenced field boundary and data
collected that was processed and analyzed as
a GIS layer or layers to generate nutrient or
soil amendment recommendations.
• The nutrient recommendation guidance and
recommendation equations used to convert the
GIS base data layer or layers to a nutrient
source material recommendation GIS layer or
layers.
• Documentation of any variable rate nutrient or
soil amendment application was made.
• Provide application records per management
zone or as applied map within individual field
boundaries (or electronic records)
documenting source, timing, method, and rate
of all applications that resulted from use of the
precision agriculture process for nutrient or soil
amendment applications.
• Maintain the electronic records of the GIS data
layers and nutrient applications for at least 5
years.
• Nitrogen recommendations based on
appropriate crop RYE and soils information
The plan was developed based on the current
NRCS 590 standard and Federal, state, or local
regulations or policies. Changes in laws or
regulations may require a plan modification.
This Implementation Requirement is a required
supplement to the Nutrient Management Plan.
Nitrogen Leaching Index Values
Nitrogen Leaching Index values, obtained through
use of current Soil Hydrologic Group (SHG)-based
LI index maps in Sec II of the NC FOTG or RUSLE
2 field -specific soil loss calculations, are included
in the Nutrient Management Plan. SHGs per soil
map unit are available through selection of the Soil
Data Explorer and Soil Properties and Qualities
(then select "Soil Qualities and Features") tabs
once an Area of Interest has been defined in
NRCS Web Soil Survey.
If the Nitrogen Leaching Index > 10 for planned
fields, appropriate conservation practices must be
planned to prevent nitrogen from leaving the field
via surface or subsurface runoff.
ADDITIONAL PHOSPHORUS -RELATED
PLAN INFORMATION
In NC, a field -specific Phosphorus Loss
Assessment Tool (PLAT) evaluation is completed
in accordance with 590 Nutrient Management
standard General Criteria requirements, and
phosphorus must be applied in accordance with
590 standard Manure Phosphorus Application
Rates.
In addition to the basic plan components, plan
information on PLAT categorical ratings, P
drawdown strategies, and conservation practices
to reduce P loss risk is required when increases in
Soil Test P are expected on the planned area.
Typically, this could occur when manure is
consistently applied at Nitrogen -based rates. High
levels of phosphorus in the surface soil layer have
been linked to increasing risk of P loss through
surface runoff and leaching.
R/1 Increases in Soil Test P are expected on
the planned area.
PLAT Cateaorical Ratinas Information
When soil test phosphorus continues to increase
on a long term basis, PLAT may produce results
that require P-based manure application planning
and planning for no additional manure P.
Conditions that will require P-based or no-P
planning will be based on site specific resource
conditions, which will facilitate data input into
PLAT. PLAT categorical ratings that will require
enhanced P application planning are:
HIGH: P-based manure application is required
(limited to P uptake in harvested crop biomass)
VERY HIGH: No additional manure P or starter P
application to be specified in nutrient management
plan.
Phosphorus Drawdown Strategy
Information:
Implementation of a phosphorus `drawdown'
strategy may be a consequence of PLAT results,
or may be requested in order to lower soil test
phosphorus levels.
Should a reduction in soil test P be desired or
necessary, the only currently proven method of
Implementation Requirements- page 2 of S North Carolina NRCS
Nutrient Management (590) August 2019

substantial P `drawdown' is to not apply manure -
based P and to plant and harvest crops that utilize
P currently present in the soil surface.
Crop specific estimated annual P removal amounts
are available on the NCSU Nutrient Management
in NC website:
hftp://nutrients.soil.ncsu.edu/vields/index.php
Conservation Practices and Management
Techniaues to Reduce P Loss Potential:
Conservation practices, especially those that
prevent soil particle detachment and trap sediment
at field edges are effective in preventing
phosphorus movement from the planned site.
Manure application techniques can also be applied
to reduce P loss risk. These practices must be
included in the conservation plan where
determined PLAT risk = HIGH for planned fields.
Consult the conservation plan developed in
conjunction with the nutrient management plan for
information on practices recommended to reduce
phosphorus AND nitrogen loss risks. Application
management techniques to reduce nutrient loss
nsK may be prescrlbea below:
Nutrient Management
Long Term Strategy for Reduction of Soil P
Levels:
As noted in the P drawdown strategy section, the
only currently proven method for reducing high
levels of soil P is not applying P, paired with
producing crops on the planned site that use
existing soil P. Where soil P and PLAT
evaluations indicate an increasing risk to water
quality, substantially reducing soil P levels through
crop uptake can take many years of
implementation.
Manure P produced in excess of crop
requirements:
Consult the nutrient management plan for a
quantification of manure generated by the animal
feeding operation that may exceed crop P
requirements.
Phosphorus "Low Risk" documentation:
PLAT is applicable to planned fields when P will be
applied at a rate above NCDA soil test report rate
guidelines for the planned crop or when the
planned area is within an `impaired' watershed and
ag-related P has been identified as a contributor to
the impairment. However, PLAT is not required
where specific conditions exist that the NC
Interagency Nutrient Management Committee (NC
INMC), composed of nutrient management
specialists from NCDA, NC DENR, NCSU, and
NRCS, has determined reflect a low risk of
phosphorus loss from the planned field.
In NC, PLAT is required if any of the following
conditions apply to the planned field:
• A field -specific PLAT assessment has never
been completed OR the last PLAT field
assessment is greater than 5 years old
• Manure sludge (as is typical with lagoon
sludge maintenance or lagoon closures) has
been applied since the last PLAT field
assessment,
• The previous PLAT Total P rating score is
greater than 45
• The planned area is to be included in land
application of lagoon sludge through closure or
maintenance
Where `low risk' conditions exist on planned fields
and a PLAT evaluation is not completed, fields and
applicable low risk condition may be documented
in the nutrient management plan narrative section
or conservation planning assistance notes.
NUTRIENT MANAGEMENT PLAN
DEVELOPMENT
The nutrient management plan has been
developed to meet nutrient application rate criteria
for all sources of nitrogen, phosphorus, potassium
as specified by NRCS 590 Nutrient Management
standard criteria.
In addition to NCDA soil test recommendations, the
plan is based on NC INMC approved values for
realistic yield goals, nitrogen factors, phosphorus
removal rates, default nutrient values for animal
waste, plant availability coefficients for N, P, and K,
and animal waste generation volumes where
applicable. Approved values are found at:
http://nutrients. soil. ncsu. edu/index. htm
Where manure is applied, farm records may also
be used through a procedure provided in SB 1217
Interagency Group guidance, available at:
http://www. nca pr. gov/SWC/techII217committee. ht
ml
Implementation Requirements- Page 3 of S North Carolina NRCS
Nutrient Management (590) August 2019

For NC permitted animal operations, planning
requirements for Plan "Amendments" (minor
modifications) and "Revisions" (Major
Modifications) are clarified by SIB 1217 Interagency
Group Guidance.
"Third Party Applicator" Information
All manure waste applied on land owned by or
controlled by the Animal Feeding Operation (AFO)
owner or operator must be included in the nutrient
management plan. The volume difference in total
manure waste generated by the AFO and waste
applied to land not owned or controlled by the
producer must be accounted for in a nutrient
management plan.
General information on manure waste generated
by an AFO to be applied to land not owned or
controlled by the AFO owner or operator may be
recorded as specified in the NC CNMP
Certification Sheet and Documentation Checklist or
other supplemental documentation to the nutrient
management plan. NRCS CNMP technical criteria
require documentation of manure exports off the
farm. The AFO owner/operator should provide the
third party applicator with a current waste analysis
in order to facilitate agronomic crop application of
the facility's generated waste. Should land not
owned or controlled by the AFO owner or operator
be included in a nutrient management plan, the
complete plan must meet 590 criteria.
RECORDKEEPING
Waste reports from the NCDA & CS Agronomic
Division, or equivalent, are acceptable sources of
information for determining applied manure nutrient
amounts for recordkeeping or crop budgeting
purposes.
Records must be maintained for at least 5 years, or
for time and manner required by Permit for animal
operations to document plan implementation and
maintenance. As applicable, records include:
• soil, plant tissue, water, manure, and
organic by-product analyses resulting in
recommendations for nutrient application,
• quantities, analyses and sources of
nutrients applied,
• dates, and method(s) of nutrient
applications, source of nutrients, and rates
of application,
• weather conditions and soil moisture at the
time of application; lapsed time to manure
incorporation; rainfall or irrigation event,
• crops planted, planting and harvest dates,
yields, nutrient analyses of harvested
biomass, and crop residues removed,
• dates of plan review, name of reviewer,
and recommended changes resulting from
the review, and
• all enhanced efficiency fertilizer products
used.
Additional records for precision/variable rate
sites must include:
• maps identifying the variable application
source, timing, amount, and placement of
all plant nutrients applied, and
• GPS-based yield maps for crops where
yields can be digitally collected.
OPERATION AND MAINTENANCE
The producer is responsible for safe operation and
maintenance of this practice, including all
equipment. Review the plan periodically to
determine if adjustments or modifications to the
plan are needed. In NC, animal operations
permitting provisions may specify more frequent
review periods. Adhere to the following operation
and maintenance provisions:
• Protect fertilizer and organic by-product
storage facilities from weather and accidental
leakage or spillage.
• Properly calibrate application equipment to
ensure uniform distribution of material at
planned rates.
• Workers should be protected from and avoid
unnecessary contact with inorganic fertilizers
and organic by-products. Extra caution must
be taken when handling ammonia sources of
nutrients, or when dealing with organic wastes
stored in unventilated enclosures.
The disposal of material generated by the
cleaning of nutrient application equipment
should be accomplished properly. Excess
material should be collected and stored or field
applied in an appropriate manner. Excess
material should not be applied on areas of high
potential risk for runoff or leaching.
• Disposal or recycling of nutrient containers
should be done according to state and local
guidelines or regulations.
Implementation Requirements- page 4 of S North Carolina NRCS
Nutrient Management (590) August 2019

ty p according �w•.
Certify and document installation of conservation radices accordin to &.law Fxi i�
`._ .r._ e.. and applicable conservation practice Statement of Work (SOW) found in Section IV of the eFOTG.
(Anyone can prepare Implementation Requirements (IR), granted it is reviewed and approved by an individual with appropriate Design JAA)
IR Prepared by (Name & Title): Sam Bingham, Engineer Date: 3�202' Project JAA Class:_
-------------------------------------------------------------------- -----------------------------
(Individuals with appropriate Design JAA can prepare, design, and approve their own work)
Design Approved by (Name & Title): Sam Bingham, Engineer
(Anyone can review the IR with the Client/Producer,
Date: 11/2022 Design JAA Level:
----------------------------------------------- ----
been approved by an individual with appropriate Design JAA)
Implementation Requirements Reviewed with the Client/Producer on inser date): 11/2022
Rocky Creek Dairy, Ben Shelton
Printed Producer Name Pro user Signature
I. Practice Installation
(Anyone can perform Practice Installations, granted it is
technical supervision of an individual with appropriate C&C JAA)
Pre-Construction/Implementation meeting completed with Client/Contractor on (insert date):
Completed By (Name & Title):
Date: C&C JAA Level:
Implementation TA provided by (Name & Title): Date:
Implementation TA provided by (Name & Title): Date:
II. On -Site Practice Inspection & Checkout {
(Anyone can perform On -Site Practice Inspections & Checkouts, granted it is certified by an individual with appropriate C&C JAA)
Amount Completed:
Remarks:
Checkout by (Name & Title):
(units) (Note: Take picture(s) and mark As -Built location on practice certification map)
Ill. Construction/Installation Certification
Date: C&C JAA Level:
(Only individuals with appropriate C&C JAA can validate and approve Construction/Installation certifications)
This practice meets MRCS standards and specifications: ❑ Yes ❑ No (If No, state reason(s) in remarks section below).
Remarks:
Certification by (Name & Title):
Date: C&C JAA Level:
Implementation Requirements- Page S of S North Carolina NRCS
Nutrient Management (590) August 2019