040036_Application_20240329

State of North Carolina
Department of Environmental Quality
Division of Water Resources
Animal Waste Management Systems
Request for Certification of Coverage
Facility Currently covered by an Expiring Sate Non -Discharge General Permit
On September 30, 2024, the North Carolina State Non -Discharge General Permits for Animal Waste Management Systems will
expire_ As required by these permits, facilities that have been issued Certificates of Coverage to operate under these State
Non -Discharge General Permits must apply for renewal at least 180 days prior to their expiration date, Therefore, all applications
must be received by the Division of Water Resources by no later than April 3, 2024.
Please do not leave any question unanswered. Please verify all information and make any necessary corrections below.
Application must be signed and dated by the Permittee.
1. Certificate Of Coverage Number: AWC 440036
2. Facility Name: White Rock Farm Dai
3. Permittee's Name (same as on the Waste Management Plan): White Rock Farms LLC
4. Permittee's Mailing Address: PO Box 10
City: Marshville
State: NC
Zip: 28103
Telephone Number: 704-221-1705 Ext. E-mail: white rock farmsOayahoo.com
5. Facility's Physical Address: 1474 Jo Pennie Rd ID
City: Peachland Jo Pet (� "St e: NC Zip: 28133
(rX0 S P C10
6. County where Facility is located: Anson
7. Farm Manager's Name (if different from Landowner): 'KOMI flog-T e
S. Farm Managers telephone number (include area code): -70 Ll ` 2 Z i - 17 ar
9. integrator's Name (if there is not an Integrator, write "None"): r4 Ot�l C .rr
10. Operator Name (OIC): ,,J05kAUP' L-."PVP.5�12 Phone No.:��`i-STR-3bflO1C#: 99-1 0
11. Lessee's Name (if there is not a Lessee, write "None"): N a N F
12. Indicate animal operation type and number:
Current Permit:
Operations Type
Allowable Count
Cattle - Dry Cow
130
Cattle - Dairy Heifer
225
Cattle - Milk Cow
700
Oneralion Tvues:
Swine
Cattle
Dry Po_ultry
Other Tines
Wean to Finish
Dairy Calf
Non Laying Chickens
Horses - Horses
Wean to Feeder
Dairy Heifer
Laying Chickens
Horses - Other
Farrow to Finish
Milk Cow
Pullets
Sheep- Sheep
Feeder to Finish
Dry Cow
Turkeys
Sheep - Other
Farrow to Wean
Beef Stocker Calf
Turkey Pullet
Farrow to Feeder
Beef Feeder
Boar/stud
Beef Broad Cow
Wet Poultry
Gilts
Other
Non Laying Pullet
Other
Layers

13. Waste Treatment Lagoons, Digesters and Waste Storage Ponds (WSP): (Fill/Verify the following information.
Make all necessary corrections and provide missing data.)
Structure
Name
Structure Type
(LagoonfDigester/
WSP)
Estimated
Date
Built
Liner Type
(Clay, Synthetic,
Unknown)
Capacity
(Cubic Feet)
Estimated
Surface Area
(Square feet)
Design Freeboard
'Redline"
(Inches)
I
Waste Pond
11/13/2012
Full, Clay
141,655.00
26,394.00
24.00
Submit one (1) copy of the Certified Animal Waste Management Plan (CAWMP) with this completed and signed
application as required by NC General Statutes 143-215.IOC(d), either by mailing to the address below or sending it via
email to the email address below.
The CAWMP must include the following components:
I. The most recent Waste Utilization Plan (WUP), signed by the owner and a certified technical specialist, containing:
a. The method by which waste is applied to the disposal fields (e.g. irrigation, injection, etc.)
b. A map of every field used for land application (for example: irrigation map)
c. The soil series present on every land application field
d. The crops grown on every land application field
e. The Realistic Yield Expectation (RYE) for every crop shown in the WUP
f. The maximum PAN to be applied to every land application field
g. The waste application windows for every crop utilized in the WUP
h. The required NRCS Standard specifications
2. A site map/schematic
,/3. Emergency Action Plan
V 4. Insect Control Checklist with chosen best management practices noted
-5. Odor Control Checklist with chosen best management practices noted
-`6. Mortality Control Checklist with selected method noted - Use the enclosed updated Mortality Control Checklist
7. Lagoonlstorage pond capacity documentation (design, calculations, etc.) Please be sure the above table is
accurate and complete. Also provide any site evaluations, wetland determinations, or hazard classifications that may be
applicable to your facility.
8. Operation and Maintenance Plan
If your CAWMP includes any components not shown on this list, please include the additional components with your submittal.
(e.g. composting, digesters, solids separators, sludge drying system, waste transfers, etc.)
I attest that this application has been reviewed by me and is accurate and complete to the best of my knowledge. I understand that,
if all required parts of this application are not completed and that if all required supporting information and attachments are not
included, this application package will be returned to me as incomplete.

Note: In accordance with NC General Statutes 143-215.6A and 143-215.613, any person who knowingly makes any false
statement, representation, or certification in any application may be subject to civil penalties up to $25,000 per violation. (18
U.S.C. Section 1001 provides a punishment by a fine of not more than $10,000 or imprisonment of not more than 5 years, or both
for a similar offense.)
Print the Name of the Perm i ttee/Landowner/S ign ing Official and Sign below. (If multiple Landowners exist, all landowners
should sign. If Landowner is a corporation, signature should be by a principal executive officer of the corporation):
Name (Print): J05AOP' l_ , Pj KSE�
Signature:
Name (Print):
Signature:
Name (Print):
Signature:
Title: ( EI'Y\ QE 2 M AlLi AG-E2
Date: Z/ z. °/ Z o z y
Title:
Date:
Title:
Date:
THE COMPLETED APPLICATION SHOULD BE SENT TO THE FOLLOWING ADDRESS:
E-mail: [e-mail]
NCDEQ-DWR
Animal Feeding Operations Program
1636 Mail Service Center
Raleigh, North Carolina 27699-1636
If you have any questions regarding this application or the general permits, please call [phone].

White Rock Farms
Combined Application Plan
(contains Pear Orchard &Twin Oaks Swine, and White
Rock Dairy)
This plan has been prepared for:
While Rock Farms
Roddy Purser
PO Box 10
Marshville. NC 28103
1011912022
This plan has been developed by:
USDA/NRCS
Richard Pigg
3230-6 Presson Rd
Monroe, NC 28110
704-324-9222
Developer Signature
Type of Plan: Nutrient Management with Manure Only
Owner/Manager/Producer Agreement
I (we) understand and agree to the specifications and operation and maintenance procedures
established in this nutrient management plan which includes an animal waste utilization plan for
the farm named above. I have read and understand the Required Specifications concerning animal
waste management that are included with this plan.
Srgnalure (owner)
Y Signature (manager or producer)
7 Z
Date
I
Z-
Date
This plan meets the minimum standards and specifications of the U.S.Department of Agriculture -
Natural Resources Conservation Service or the standard of practices adopted by the Soil and Water
Conservation Commission.
Plan Approved By: —
Technical Specialist Signature Date

®I
Sources in Plan
White Rock Farms
S 8
Dairy (Milk Cow) Liquid Manure Slurry waste generated 4,068,225 galslyear by a 525 Dairy (Milk
Cow) Liquid Manure Slurry operation This production facility has waste storage capacities of
approximately 180 days
Estimated Pounds of Plant Available Nitrogen Generated per Year
Injected
40,756
Incorporated-4 wks or less
following application
40,756
Incorporated-5 wks to 3 mos
following application
27,170
Broadcast
27.170
Irrigated
27,170
Max Available
PAN (€bs) '
Actual PAN
Applied (Ibs)
PAN Surplus 1
Deficit (Ibs)
Actual Volume
Applied (Gallons)
volume SurplusDeficit
(Gallons)
Year 1
27.170
39.746
(12,576)
5,951.332
(1,883,107)
Year 2
27,170
26.853
317
4,020.757
47,468
Year 3
27,170
36,211
(9 041)
5,422,023
(1,353.798)
12/1412023 4.11 07 PM 214

Sources in Plan
White Bock Farms
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Sources in Plan
White Rock Farms
39
Dairy (Milk Cow) Solid waste generated 1,666 tons/year by a 98 Dairy (Milk Cow) Solid operation
Estimated Pounds of Plant Available Nitrogen Generated per Year
Injected
11,196
Incorporated-4 Wks or less
following application
11,196
Incorporated-5 Wks to 3 mos
following application
7,464

Sources in Plan
White Rock Farms

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Required Soil Test Values
White Rock Farms
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
excess t plant
growth Alternative crop sites must be used when the concentration of these metals approach
levels
Site life can be estimated by dividing the amount of copper and zinc to be applied In Ibsfacre 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 sod sample. Application of lime at recommended rates is
op
e first
rnecessary to ecommendationistmay needHto beereevaluated to enfor sureroptimalliranigeslofricrop prodpu�iontation are maintained these
in optimum range
pH
5 1
47
62
Lime Recom,
for Crop(s)
(tons/acre)
0.0
0 0
0.0
Cu-I
27
45
55
Copper
Recommendation
0, 0
0, 0
0,0
Zn-I
47
28
62
Zinc
Recommendation
0, 0
0. 0
0.0
Tract ID
Field ID
Crop(s)
OOO6NG
6
0011HT
11
E
00125C
12
6
0, 0
0
0. 0
0
D, 0
161
1
67
0,0
0
0.0
0
0,0
930
9
936
7
69
0.0
71
0,0
0
0,0
--
69
0.0
80
0. 0
11 p
0. 0
936
8
7
D, 0
0
0. 0
0
0, 0
10010
2
10062
4
6
0
0,0
g
0.0
0
0.0
0
0.0
10486
3
73
0.0
0
0.0
r8217
5
Zinc and Copper Toxicity Levels in Soils
Metal
Soil Test Index
Recommended Action
Zn
300
Limit application on peanuts Maintain soil pH >= 60
500
Cease application on peanut land Mamlain sod pH >= 6 0
2000
Caution seek alternative s tc (all crops) Maintain sod pH >= 6 0
3000
Cease application (all crops) Maintain sod pH >= 6 0
Cu
2000
Caution seek alternative site (all crops) Maintain soil pH >= 6 0
I
3000
Cease application (all crops) Maintain sod pH >= 6 0.
12f14/2023 4 11 52 PM 1 ! 1

J
Planned Crops Summary
White Rock Farms
The table shown below provides a summary of the crops or rotations Included in the plan for each field. Realistic Yield estimates
and Plant Available Nitrogen (PAN) recommendations are also provided for each crop as well as the crop's P205 Removal Rate.
The Leaching Index (LI) and the Phosphorous Loss Assessment Tool (PLAT) Rating are also provided for each field, where
available,
If a filed's PLAT Rating is High, any planned manure application is limited to the phosphorous removal rate of the harvested plant
biomass for the crop rotation or multiple years in the crop sequence Fields with a Very High PLAT Rating should receive no
additional applications of manure. Regardless of the PLAT rating starter fertilizers may be recommended in accordance with
North Carolina State University guidelines or recommendations. The quantity of P205 applied to each crop is shown in the
following table if the field's PLAT rating is High or Very High
Tract Field Total E Wettable SMU it Crop Name ` RYE Recom- PLAT P205 (lbslacre)
Acres Acres mended Rating ilCrop
PAN Removal Applied
0 6NG 6 150 14T CrB 9
Corn, Silage a — 114 Tons 116 Medium 39 NA
Small Grain, Silage 6,7Tons 69 Medium 36 NA
Grain Sorghum, Silage 97 Tons 69 Medium 29 NA
T Mixed Cool Season Grass -Pasture 2.4 Tons 74 Medium! 3 NA
0011 HT 11 43 _ 425. I BaC 9
Corn, Silage 17-6 Tons 188 Medium 60 NA
Small Grain, Silage—� 8 Tons 86 Medium 43 NA
Grain Sorghum, Silage 15 Tons 112 Medium 45 NA
Mixed Cool Season Grass -Pasture 2.2 Tons 71 Medium 3 NA
0012SC 1 121 38.61 381 CrBi 91 1
161 1 75.7 75 CnA
930 91 70.8 70 BaC
Corn, Silage
11.4 Tons
116
Low
39
NA.
Small Grain, Silage —
Grain Sorghum, Silage
- --- --—
Mixed Cool Season Grass -Pasture
6 7 Tons
69
Low
36
NA
NAE
I
NA
9.7Tons
69
-- v
Low
29
2.4 Tons
74
Low
—
3
Corn, Silage 12 Tons 128 Low 41 NA,
Small Grain, Silage 7 Tons 76 Low 38 NA',
Grain Sorghum, Silage 10.2 Tons 76 Low 31 NA
Mixed Cool Season Grass -Pasture 2 8 Tons 90 Low — 4 NA'
Corn, Silage 17 6 Tens 188 Low 60 NA
Small Gram, Silage W 8 Tons 86 Low 43 NA
Grain Sorghum, Silage 15 Tons 112 Low 45 - NA'
Mixed Cool Season Grass•Paslure 2.2 Tons 71 Low T 3 NA'
12/1412023 4 11 31 PM 1 13

Planned Crops Summary
White Rock Farms
29 7 29 MIR 9
Corn Silage 19 Tors', 194 ! Medaurn 6S NA
Small Grain, Silage 86 Tons 89 Medium 4 NA
Gram Sorghum, Silage 16 1 Tons 114 Medium 48 NA
Mixed Cool Season Grass -Pasture 3 3 Tons 101 Medium 5 NA
93fi 8 20 4 20 - M; B 9 _
L"rn. Silage 19 Tons • 194 — Low 65 NA
Small Gram, Silage 8 6 Tons f 89 Low 46, NA
I
MixedCool Season Grass -Pasture 3 3 Tons II 1 o1 Low 5 NA
Grain Sorghum, Silage 16 1 Tons 114, Low 48 NA
--
ionto 2 923 Jj2nA 9 -- -- —,—
Corn, Silage12 Tons 128 Medium i 41 I NA
Small Grain, Silage 7 Tons 76 Medium 38 NA
Gram Sorghum, Silage 10 2 Tons 76 Medium 311 NA
Mixed Cool Season Grass -Pasture 2 8 Tons 90 Medium 4 NA
10062 4' 1792 176 CrB� 9
Corn, Silage 11.4 Tons 116 Low 39. NA
Small Grain, Silage 6 7 Tons 69 Low 361 NA
Grain Sorghum, Silage -9—7 Tons — 69 Low 29 NA
Mixed Cool Season Grass -Pasture 2 4 Tons 74 Low 3 NA
10466 { 88.1 87. MMaB 9 -
Corn, Silage 19 Tons 194 Low 65 NA
Small Grain. Silage 8 6 Tons 89 _ Low 46 NA
Grain Sorghum, Silage 16 1 Tons 114 Low 48 NA
Mixed Cool Season Grass Pasture 3 3 Tons 101 Low 5 NA
11821 5�120�-_-116i
Corn, Silage 11,4 Tons 116 Law 39 NA
Small Grain, Silage 6 7 Tons 69 Low 36 NA
Grain Sorghum, Silage 9 7 Tons 69 Low 29� NA
Mixed Coal Season Grass -Pasture 2 4 Tons 74 Low 3 NA
Totals: 9o7 80 893001
Notes 1 In the tract column, - symbol means leased, otherwise, owned
12/14/2023 4 11 31 PM 2 13

Planned Crops Summary
White Rock Farms
LI
Potential Leaching
Technical Guidance
None
Low potential to contribute to soluble nutrient
<2
leaching below the root zone.
Moderate potential to contribute to soluble nutrient
Nutrient Management (590) should be planned
' = 2 & < = 10
leaching below the root zone-
Nutrient Management (590) should be planned. Other conservation
High potential to contribute to soluble nutrient
f leaching below the root zone.
practices that improve available water holding capacity of sal and
improve nutrient use efficiency should be considered. Examples are
> 10
Cover Crops (340) to scavenge nutrients, Sod -Based Rotations (328),
Long -Term No -Till (778), and edge -of -field practices such as Filter
Strips(393) and Riparian Forest Suffers (391).
P Loss Index Rating
P Management Recommendation
�- 0 - 25 Low
i
No adjustment needed; N based application
26 - 50 Medium
No adjustment needed; N based application
51 - 100 High
Application limited to crop P removal
i > 100 Very High
E Starter P application only
12/14/2023 4 11 31 PM 313

Required Specifications For Animal Waste Management
i. 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.
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.
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.
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, MRCS Field Office Technical
Guide Standard 393 - Filter Strips).
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.

5. 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.
io 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.
ii 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.
15. 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.
n. 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.
1g. 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.

20. 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

l i131
■r1� �
NUTRIENT MANAGEMENT PLAN
SUPPLEMENTAL INFORMATION
N C Practice Job Sheet NC-590
Prepared
By:
5
Farm: Tract(s): 5�_
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
The following components are included in
nutrient management plan specifications
typical of more 'traditional'
Date:U_L?j_Z
fertilizer and manure application methods.
When precision aglvariable rate application
technology is utilized, see the next section of
this Job Sheet for additional guidance on plan
requirements.
• aerial site photograph(s)limagery or site
map(s), and a soil survey map of the site.
• Sufficient soils information —such as dominant
sod 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 nsk assessment tools for
any necessary evaluations for nitrogen,
phosphorus, and erosion losses_
• current andlor planned plant production
sequence or rotation,
• soil, water, compost, manure, organic by-
product, and plant tissue sample analyses
applicable to the plan Where non-NCDA soil
testing labs are used, nutrient
recommendations must be made using NCDA-
similar guidelines and methodologies. Note.
high levels of sal copper and zinc may be toxic
to production crops. Land application of these
nutrients must be accordance with
NCSUlNCDA crop toxicity guidelines.
Realistic yield goals for the crops planned for
nutrient application,
NC-390 Job Sheet May 2015 page t

• Planned nitrogen application rates based on
NC Realistic Yield Expectations (RYEs) or
sufficiently documented yield records,
• The Nitrogen Leaching Index for planned
fields,
• Planned P & K application rates based on soil
test results (see next section where P & K
applied through variable rate technology).
• listing and quantification of all nutrient sources
and form, including starter fertilizer
applications and legume -based cover crop
mixes.
• 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
• guidance for implementation, operation and
maintenance, and recordkeeping as specified
by the CNMP or applicable NC DWQ or
NDPES permit
Where precision/variable rate nutrient
application applications are planned and
made, some required planning components of
the preceding section may be provided by the
overall conservation plan. In addition, 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
sod amendment recommendations.
• Planned nitrogen application rates based on
NC RYEs or sufficiently documented yield
records
• The Nitrogen Leaching Index for planned
fields.
• 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.
• Soil testing documentation that crop
Phosphorus (P205) and Potassium (K20)
nutrient or soil amendment application will be
made per soil test results similar to NCDA
guidelines. Where P & K will not be applied
via variable rate application technology, but by
basic GPS guidance, recommended P & K
NC-590 Job Shed May 2015
rates must be provided as specifications prior
to application.
• Note —where Diammonium phosphate (18-46-
0) is the primary variable rate P fertilizer
source applied on legume crops, additional N
will likely be needed to achieve RYEs.
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 Jot? Sheet is a required supplement to
the Nutrient Management Plan,
NC Permitted Animal Operations: For NC
DENR-DWR or NPDES permitted animal
operations, the waste utilization portion of the
Certified Animal Waste Management Plan
(CAWMP) must meet requirements specified by
the Permit. The NC 1217 Interagency Group
provides guidance on the required minimum
elements of a CAWMP. This guidance is found in
Sec 1.1 of the latest 1217 Guidance Document,
located at:
http://www.ncaqr-(Iov/SWC/tech/quidancedocumen
ts.html
Nitrogen Leaching Index Values
Nitrogen Leaching Index values, obtained through
use of current Soil Hydrologic Group SFIG -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 Sod
Data Explorer and Soil Properties and Qualities
(then select "Sod 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
included in a conservation plan to prevent nitrogen
from leaving the field via surface or subsurface
runoff.
Below are conservation crop management
techniques and practices recommended for
mitigation of nitrate losses (practices also
documented in conservation plan):
l�EW
/! _/ 4
C/`D S GG�rS
page 2

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 Agronomic Division soil test
recommendations, or soil test recommendations
made through similar guidelines, 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 IN, P, and K, and animal
waste generation volumes where applicable.
Approved values are found at:
httpYlnutnentssort. 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 •1/www ncagr gov/SWCltech11217committee. ht
rMl
For NC permitted animal operations, planning
requirements for Plan "Amendments" (minor
modifications) and "Revisions" (Major
Modifications) are clarified by SB 1217 Interagency
Group Guidance.
ADDITIONAL PHOSPHORUS -RELATED
PLAN INFORMATION (Applicable when
increases in Soil Test P are expected on
the planned area)
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 Nilrogen-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.
Increases in Soil Test P are expected
on the planned area (not typical if P
application made per soil test results).
NC-590 Job Sheet May 2015
PLAT Categorical Ratings 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 specfied 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
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:
http_l/nutrients soil.ncsu edulyieldshndex,p
Conservation Practices and Management
Techniques 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
risk may be prescribed below:
page S

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 sod P and PLAT
evaluations indicate an increasing risk to water
quality, substantially reducing sod P levels through
crop uptake can take many years of
implementation. When P is not applied, and
existing soil P is used by crops, eventually, soil will
become P deficient. Consult CES or NCDA
Regional Agronomy specialists for additional
information sod test P reduction timelines.
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.
"Manure Hauler" 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 CLAMP
Certification Sheet and Documentation Checklist or
other supplemental documentation to the nutrient
management plan. NRCS CNMP technical criteria
require documentation of manureexportsoff the
farm this can be done below 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
Type and Quantity of Animal Feeding Operation
(AFO) manure generated by the facility
Quantity of AFO manure generated to be exported
off the farm for third party application:
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.
Documentation per field nitrogen
application rates do not exceed RYE -
based recommended rates
• Documentation that applied phosphorus
and potassium recommendations do not
exceed recommended rates specified by
soil tests
For non -variable rate application of P & K,
provide applied map with field boundaries
indicating source, timing, method, and rate
of all applications
Where 'chlorophyll reader' technology is
utilized, application records that nitrogen
rates match RYE -based N rates as closely
as possible.
.NC-590 Jot) Shcot May 2015 page 4

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-
NC-590 Job Sheet May 2015 page 5

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.
z. 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.
a. 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, MRCS 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).
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 pending
should occur in order to control odor and flies
8. Animal waste shall not be applied to saturated soils, during rainfall events, or
when the soil surface is frozen.
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.
io. 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.
1i. 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.
m Waste shall be applied in a manner not to reach other property and public
right-of-ways.
is. 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.
is. 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.
is. 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.
i90 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.

zo. 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.
zz. 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.

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EMERGENCY ACTION PLAN
PHONE NUMBERS
DWQ
EMERGENCY MANAGEMENT SYSTEM
SWCD
NRCS
This plan will be implemented in the event that wastes from your operation are leaking,
overflowing, or running off site. You should not wait until wastes reach surface waters or leave
your property to consider that you have a problem. You should make every effort to ensure that
this does not happen. This plan should be posted in an accessible location for all employees at the
facility. The following are some action items you should take.
1. Stop the release of wastes. Depending on the situation, this may or may not be possible.
Suggested responses to some possible problems are listed below.
A. Lagoon overflow -possible solutions are:
a. Add soil to berm to increase elevation of dam.
b. Pump wastes to fields at an acceptable rate.
c. Stop all flows to the lagoon immediately.
d. Call a pumping contractor.
e. Make sure no surface water is entering lagoon.
B: Runoff from waste application field -actions include:
a. Immediately stop waste application.
b. Create a temporary diversion to contain waste.
c. Incorporate waste to reduce runoff.
d. Evaluate and eliminate the reason(s) that caused the runoff:
e. Evaluate the application rates ibr the fields where runoffoccurred.
C: Leaka,,c from the waste pipes and sprinkiers-action include:
a. Stop recycle pump.
b. Stop irrigation pump.
c. Close valves to eliminate further discharge.
d. Repair all leaks prior to restarting pumps.
December 18, 1996

1, f
D: Leakage from flush systems, houses, solid separators -action include:
a. Stop recycle pump.
b. Stop irrigation pump.
c. Make sure no siphon occurs.
d. Stop all flows in the house, flush systems, or solid separators.
e. Repair all leaks prior to restarting pumps.
E: Leakage from base or sidewall of lagoon. Often this is seepage as opposed to flowing;
leaks- possible action:
a. Dig a small sump or ditch away from the embankment to catch all seepage, put In a
submersible pump, and pump back to lagoon.
b. If holes are caused by burrowing animals, trap or remove animals and fill holes and
compact with a clay type soil.
c. Have a professional evaluate the condition of the side walls and lagoon bottom as soon
as possible.
2, Assess the extent of the spill and note any obvious damages.
a. Did the waste reach any surface waters?
b. Approximately ]low much was released and for what duration?
c. Any damage noted, such as employee injury, fish kills, or property damage'?
d. Did the spill leave the property'?
e. Does the spill have the potential to reach surface waters?
f. Could a future rain event cause the spill to reach surface waters?
g. Are potable water wells in danger (either on or off of the property)?
h. How much reached surface waters?
3: Contact appropriate agencies.
a. During normal business hours, call your DWQ (Division of Water Quality) regional office,
Phone - - . After hours, emergency number: 919-733-3942. Your phone call
should include: your name, facility, telephone number, the details of the incident from item
2 above, the exact location of the lacihty, the location or direction of movement of the
spill, weather and wind conditions. The corrective measures that have been under taken,
and the seriousness of the situation.
b. Ifspill leaves property or enters surface waters, call local EMS Phone number - -
c. Instruct EMS to contact local Health Department.
d. Contact CES, phone number - - , local SWCD office phone number - - and
local MRCS office for advice/technical assistance phone number - -
December 18, 1996

14 4
4: If none ol'the above works call 911 or the Sheriff's Department and explain your problem to
them and ask that person to contact the proper agencies for you.
5: Contact. the contractor ofyour choice to begin repair ol'problem to minimize off -site damage.
a. Contractors Name:
b. Contractors Addre
c. Contractors Phone
6: Contact the technical specialist who certified the lagoon (NRCS, Consulting Engineer, ctc.)
a. Name:
b. Phone:
7: Implement procedures as advised by DWQ and technical assistance agencies to rectify the
damage, repair the system, and reassess the waste management plan to keep problems with
release of wastes Born happening again.
December 18, 1996

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Nutrient Management Plan For Animal Waste Utilization
This plan has been prepared for:
White Rock Farms
Rodney Purser
PO Box 10
Marshville, NC 28103
704-221-1705
04-16-2019
This plan has been developed by:
Samuel Bingham
NRCS TSP
845 Baber Road
Ruthefordton, NC 28139
828-42 • 9:
Developer
Type of Plan: Nutrient Management with Both Manure and Fertilizer
Owner/Manager/Producer Agreement
I (we) understand and agree to the specifications and the operation and maintenance
procedures established in this nutrient management plan which includes an animal
waste utilization plan for the farm named above. I have read and understand the
Required Specifications concerning animal waste management that are included with
this plan.
Signature (owner Date
Signature (manager or producer) Date
This plan meets the minimum standards and specifications of the U.S. Department of
Agriculture - Natural Resources Conservation Service or the standard of practices
adopted by the Soil and Water Conservation Commission.
Plan Approved By:
dlr� &- L7-3,.,
`I`elKal Specialist Signature D to
671574 Database Version 3.1 Date Printed 04-16-2010 Cover Page 1

Nutrients applied in accordance with this plan will be supplied from the
following source(s):
Commercial Fertilizer is included in this plan.
Ul
Farrow-to-weanmorven waste generated 7,046,600 gals/year by a 2,200 animal Swine
Farrowing-Weanling Lagoon Liquid operation. This production facility has waste
storage capacities of approximately 120 days.
Estimated Pounds of Plant Available Nitrogen Generated per Year
Broadcast
15083
Incorporated
25903
Injected
28526
Irrigated
16395
Max. Avail.
PAN (lbs) *
Actual PAN
Appl ied (I bs)
PAN Surplus/
Deficit (lbs)
Actual Volume
Applied (Gallons)
Volume Surplus/
Deficit (Gallons)
Year 1
16,395
18524
-2,129
7,991,323
-944,723
Year 2
16,334
16338
-4
7,048,364
-1,764
U2
Swine mortality compost waste generated 67.98 tons/year by a 2,200 animal Swine
Farrowin -weanling operation
Estimated Pounds of Plant Available Nitrogen Generated per Year
Broadcast
1434
Incorporated
2035
Injected
N/A
Irrigated
N/A
Max. Avail.
PAN (lbs)*
Actual PAN
Applied (lbs)
PAN SurplusJ
Deficit (lbs)
Actual Quantity
Applied (Tons)
Surp Ius/Deficit
(Tons)
Year 1
1,434
1038
396
49.21
18.77
Year 2
1,434
270
1,164
12.78
55.20
This plan includes a User Defined Source to determine the total pounds of PAN in lieu
of NRCS Standard values. Refer to North Carolina Cooperative Extension Service publication AG-439-42
entitled "Soil Facts: Use of On -Farm Records for Modifying a Certified Animal Waste Management Plan" for
guidance on using on -farm records to develop a User Defined Source.
Note: In source ID, S means standard source, U means user defined source_
* Max. Available PAN is calculated on the basis of the actual application method(s) identified in the plan for this source.
Preview Database Version 3.1 Date Printed: 04-19-2019 Source Page I of I

The table shown below provides a summary ofthe crops or rotations included in this plan for each field. Realistic Yield e
are also provided for each crop, as well as the crop's P205 Removal Rate. The Leaching Index (LI) and the Phosphorous i
Assessment Tool (PLAT) Rating are also provided for each field, where available.
If a field's PLAT Rating is High, any planned manure application is limited to the phosphorous removal rate of the harvesl
biomass for the crop rotation or multiple years in the crop sequence. Fields with a Very High PLAT Rating should reeeiv
additional applications of manure. Regardless of the PLAT rating, starter fertilizers maybe recommended in accordance
Carolina State University guidelines or recommendations. The quantity of P205 applied to each crop is shown in the folic
table if the field's PLAT rating is High or Very High.
Planned Crops Summary
P205
Total
Useable
Plat
Removal I
Applied
Tract
Field
Acres
Acres
wing
Ll
Soil Series
Crop Sequence
RYE
gbsfacre)
(Ibs/acre)
10575
1
21.30
21.30
Low
10.0
Emporia
Small Grain, Silage
9.3 Tons
50
N/A
Corn, Silage
19.6 Tons
67
N/A
Grain Sorghum, Silage
:16.7 Tons
50
N/A
Small Grain, Silage
9.3 Tons
50
NIA
Grain Sorghum, Silage
16.7 Tons
50
N/A
Grain Sorghum, Silage
:16.7 Tons
50
N/A
! 05?5
2
15.10
15.10
Low
20.0
Candor
Small Grain, Silage
5.7 Tons
3I
N/A
Corn, Silage
10.0 Tonsl
34
NIA
Grain Sorghum, Silage
*8.6 Tons
26
NIA
SIn Grain, Silage
5.7 Tons
31
NIA
Grain Sorghum, Silage
*8.6 Tons
26
NIA
Grain Sorghum,.Silage
*8.6 Tons
26
N/A
10575
3
19.80
19.801
Law
15.0
Chewacla-CP
Gammagrass Hay
4.7 Tonsi
76
N/A
10575
4
1.00
1.00
Low
15.0
Nanford
Small Grain, Silage
8.8 Tons
48
NIA
Corn, Silage
21.6 Tons
73
NIA
Grain Sorghum, Silage
18.3 Tons
55
N/A
Small Grain, Silage
8.9 Tons
48
N/A
Grain Sorghum, Silage
18.3 Tons
55
NIA
Grain Sorghum, Silage
18.3 Tons
55
NIA
10*7
5
2.90
2.90
Low
15.4
Nanford
Small Crain, Silage
8.6 Tons
46
NIA
Corn, Silage
20.9 Tons
71
N/A
Grain Sorghum, Silage
17.8 Tons
53
NIA
Small Grain, Silage
8.6 Tons
46
N/A
Grain Sorghum, Silage
17.8 Tons
53
NIA
Crain Sorghum, Silage
ITS Tons
53
N/A
10575
6
1.701
1.701
Low
15.0
Chewacla-CP
Gammagrass Hay
4.7 Tons
76
NIA
PLAN TOTALS: 61.80 61.80
Preview Database Version 3. t Date Printed 411912019
PCS Page 1 of 2
NOTE: Symbol * means user entered data.

Li Potential Leaching Technical Guidance
< 2 w potential to contribute to soluble None
utrient leaching below the root zone.
> 2 & Moderate potential to contribute to Nutrient Management (590) should be planned.
soluble nutrient leaching below the
<_ 10
root zone.
High potential to contribute to soluble Nutrient Management (590) should be planned. Other conservation practices that improve
nutrient leaching below the root zone. the soils available water holding capacity and improve nutrient use efficiency should be
> 10 considered. Examples are Cover Crops (340) to scavenge nutrients, Sod -Based Rotations
(328). long -Term No -Till (778), and edge -of -field practices such as Filter Strips (393) and
Riparian Forest Buffers (391).
PLAT Index
Rating
P Management Recommendation
0 - 25
Low
No adjustment needed; N based application
25 - 50
51 - 100
Medium
High
No adjustment needed; N based application
Application limited to crop P removal
> 100
Very High
Starter P application only
671574 Database Version 3.1 Date Printed 4116/2019
PCS Page 2 of 2
NOTE: Symbol * means user entered data.

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The Irrigation Application Factors for each field in this plan are shown in the following table. Infiltration rate varies
with soils. If applying waste nutrients through an irrigation system, you must apply at a rate that will not result in
runoff. This table provides the maximum application rate per hour that may be applied to each field selected to
receive wastewater. It also lists the maximum application amount that each field may receive in any one application
event.
Irrigation Application Factors
Tract
Field
Soil Series
Application Rate
(inches/hour)
Application Amount
(inches)
10575
1
Emporia
0.50
1..0
10575
2
Candor
0.75
1.0
10575
3
Chewacla-CP
0.35
1.0
10575
5
Nanford
0.40
1.0
671574 Database Version 3.1 Date Printed 4/16/2019 IAF Page 1 of 1
NOTE: Symbol * means user entered data.

The Nutrient Management Recommendations table shown below provides an annual summary of the nutrient
management plan developed for this operation. This table provides a nutrient balance for the listed fields and crops
for each year of the plan. Required nutrients are based on the realistic yields of the chaps to be grown, their nutrient
requirements and soil test results. The quantity of nutrient supplied by each source is also identified.
The total quantity of nitrogen applied to each crop should not exceed the required amount. However, the quantity
of other nutrients applied may exceed their required amounts. This most commonly occurs when manure or other
byproducts are utilized to meet the nitrogen needs of the crop. Nutrient management plates may require that the
application of animal waste be limited so as to prevent over application of phosphorous when excessive levels of
this nutrient are detected in a field. In such situations, additional nitrogen applications from nonorganic sources
may be required to supply the recommended. amounts of nitrogen.
Nutrient Management Recommendations Test
YEAR
p
N
(lbs/A)
P205
(lbs1A)
K20
(lbs/A)
Mg
(lbs/A)
Mn
(lbs1A)
Zn
(lbs/A)
CU
(lbs/A)
Lime
(tons/A)
Tract
Field
10575
1
Req'd Nutrients
106
0
80
0
0
0
0
1
Acres
App. Period
21.30
9/1-3/31
Supplied By:
CROP
Small Grain, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
()
0
0
0
0
1
Soil Series
Emporia
Residual
0
0
0
0
0
0
0
0
RYE Sample
Date
9.3 Tons
04-12-19
Manure
106
25
269
13
0
0
0
0
P Removal
Rating
50 lbs/ac.
Low
BALANCE
0
25
189
13
0
0
0
0
Tract
Field
10575
2
Req'd Nutrients
71
0
80
0
0
0
2
0
Acres App.
Period
15.I0
1 9/1-3131
Supplied By:
CROP
Small Grain, Silage
Starter
0
0
0
U
0
0
0
0
CommercialFert,
0
0
0
0
{}
0
2
0
Soil Series
Candor
Residual
01
0
0
01
0
0
0
0
RYE I Sample
Date
5.7 Tons
04-12-19
Manure
711
16
180
8
0
0
0
0
P Removal
Rating
31 lbs/ac.
Low
BALANCE
0
16
100
8
0
0
0
0
Tract I Field
10575
4
Req'd Nutrients
95
0
8o
0
0
0
0
I
Acres App.
Period
1.00
9/1-3/31
Supplied By:
CROP
Small Grain, Silage
Starter
0
0
0
0
4
0
4
0
Commercia] Fert.
4
0
0
0
0
0
0
1
Soil Series
Nanford
Residual
0
0
0
0
0
0
0
0
RYE I Sample
Date
8.8 Tons
04-12-19
Manure
95
24
262
12
0
0
0
0
P Removal
Rating
48 lbslac.
Low
BALANCE
0
24
182
12
0
0
0
(}
Tract Field
10575
5
Req'd Nutrients
93
0
80
0
0
0
2
0
Acres App.
Period
2.90
9/1-3/31
Supplied By:
CROP
Small Grain, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fen.
0
0
0
0
0
0
1
0
,Soil Series
Nanford
Residual
0
0
0
0
0
0
0
0
RYE I Sample Date
8.6 Tons
04-12-19
Manure
93
1.38
122
30
3
2
1
0
P Removal
I Rating
46 lbs/ac.
Low
BALANCE
0
138
42
3()l
3
2
0
0
Preview Database Version 3.1 Date Printed: 4/19/2019 NMR Page 1 of 7

Nutrient Management Recommendations Test
YEAR 0
N P205 K20 Mg Mn Zn Cu Lime
Qbs/A} (1bs1A) (lbs1A) (Mg) (1bs1A} (lbs/A) (1bs1A) (tons/A)
NOTE: Symbol * means user entered data.
Preview Database Version 3.1 Date Printed: 4/19/2019 NMR Page 2 of 7

Nutrient Management Recommendations Test
YEAR
I
N
(%s/A)
P20S
(lbs/A)
K20
(lbs/A)
Mg
(lbs/A)
Mn
(lbs/A)
7n
(lbs/A)
Cu
(lbs/A)
Lime
(tons/A)
Tract Field
10575
1
Req'd Nutrients
*218
0
140
0
0
0
0
0
Acres App.
Period
21.30
2/15-6/30
Supplied By:
CROP
Corn, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Emporia
Residual
0
0
0
0
0
0
0
0
RYE Sample
Date
*19.6 Tons
04-12-19
Manure
218
1 51
552
26
0
0
0
0
P Removal
Rating
67 lbs/ac.
Low
BALANCE
0
51
412
26
0
0
01
0
Tract
Field
10575
1
Req'dNutrients
*130
0
140
0
0
0
0
0
Acres App.
Period
21.30
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
[}
Soil Series
Emporia
Residual
0
0
0
0
0
0
0
0
RYE Sample
Date
*16.7 Tons
04-12-19
Manure
130
30
329
15
0
0
01
0
P Removal
I Rating
50 lbs/ac.
Low
BALANCE
0
30
189
15
0
0
0
0
Tract
Field
10575
€
Req'dNutrients
106
0
80
0
0
0
0
0
Acres App.
Period
21.30
911-3/3l
Supplied By:
CROP
Small Grain, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Emporia
Residual
0
0
0
0
0
0
0
0
RYE I Sample
Date
9.3 Tons
04-12-19
Manure
106
25
269
13
0
0
0
0
P Removal
Rating
50 lbs/ac.
Low
BALANCE
0
25
18')l
13
0
0
0
0
Tract
Field
10575
2
Req'd Nutrients
1120
0
140
0
0
0
0
0
Acres App.
Period
15.10
2/15-6/30
Supplied By:
CROP
Com, Silage
Starter
0
0
0
0
0
0
f)
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Candor
Residual
0
0
0
0
0
0
0
0
RYE I Sample
Date
*10.0 Tons
04-12-19
Manure
120
28
304
14
0
0
0
0
P Removal
Rating
34 lbs/ac.
Low
BALANCE
0
28
164
14
0
0
0
0
Tract
Field
10575
2
Req'd Nutrients
*72
0
140
0
0
0
0
0
Acres App.
Period
15.10
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fat.
0
0
0
0
0
01
0
0
Soil Series
Candor
Residual
0
0
0
0
0
0
0
0
RICE I Sample
Date
*8.6 Tans
1 04-12-19
Manure
72
17
182
91
0
0
0
0
P Removal
Rating
26 lbs/ac.
Low
BALANCE 1
0
17
42
9
0
0
0
0
Preview Database Version 3.1 Date Printed: 4/19/2019 NMR Page 3 of 7

Nutrient Management Recommendations Test
YEAR
I
N
(1bslA)
P205
(lbs/A)
K20
(1bs/A)
Mg
(lbs/A)
Mn
(lbs/A)
Zn
(lbs/A)
Cu
(lbs/A)
Lime
(tons/A)
Tract
Field
10575
2
Req'd Nutrients
71
0
80
0
0
0
0
0
Acres App.
Period
15.10
911-3/31
Supplied By:
CROP
Small Grain, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Candor
Residual
0
0
0
0
0
0
0
0
RYE I Sample
Date
5.7 Tons
04-12-19
Manure
71
16
180
8
0
0
0
0
P Removal
I Rating
31 lbs/ac.
Low
BALANCE
0
16
100
8
0
0
01
0
Tract
Field
10575
3
Req'd Nutrients
193
110
20
0
0
0
0
0
Acres App.
Period
19.80
3/1-9/30
Supplied By:
CROP
Garnmagrass Hay
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
01
65
0
0
0
0
0
0
Soil Series
Chewacla-Cl?
Residual
0
0
0
0
0
0
()1
0
RYE I Sample
Date
4.7 Tons
04-12-19
Manure
193
45
489
23
0
0
0
0
P Removal
Rating
76 Ibs/ac.
Low
BALANCE.
0
0
469
23
0
0
0
0
Tract
I Field
10575 1
4
Req'd Nutrients
231
0
140
0
0
0
0
0
Acres App.
Period
1.00
2/15-6/30
Supplied By:
CROP
Corn, Silage
Starter
(>
0
0
0
0
0
0
(1
Commercial Fert,
0
0
0
0
0
O
0
0
Soil Series
Nanford
Residual
0:
0
0
0
0
0
0
0
RYE I Sample
Date
21.6 Tom
04-12-19
Manure
231
58
636
30
0
0
0
0
P Removal
I Rating
73 lbs/ac.
I.ow
BALANCE
0
58
496
30
0
0
0
0
Tract
Field
10575
4
Req'd Nutrients
137
0
140
0
0
0
0
0
Acres App.
Period
1.00
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Nanford
Residual
01
0
0
0
0
0
0
0
RYE I Sample
Date
18.3 Tons
04-12-19
Manure
137
35
377
18
0
0
0
0
P Removal Rating
55 Ibs/ac.
Low
BALANCE
0
35
237
18
0
0
0
0
Tract
I Field
10575
4
Req'd Nutrients
95
0
80
0
0
0
0
0
Acres App.
Period
1.00
9/1-3131
Supplied By:
CROP
Small Grain, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
l)
0
0
0
Soil Series
NanfoTd
Residual
0
0
0
0
0
0
0
0
RYE I Sample D to
8.8 Tons
04-12-19
Manure
95
24
262
12
0
3
0
0
P Removal
Rating
48 lbs/ac.
Low
BALANCE
1 01
241
182
12
0
0
0
0
NMR Page 4 of 7

Nutrient Management Recommendations Test
YEAR
1
N
(lbs/A)
P205
(lbs/A)
K20
(lbs/A)
Mg
(1bslA)
Mn
(lbs/A)
Zn
(lbs1A)
Cn
(1bs/A)
Lime
(tons/A)
Tract
FFild
16575
5
Req'd Nutrients
224
0
140
0
0
0
0
0
Acres I App,
Period
2.90
2/15-6/30
Supplied By:
CROP
Com, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Nanford
Residual
0
0
0
0
0
0
0
0
ple Date
20.9 Tons
04-i2-19
Manure
224
332
294
72
6
6
Rating
71 lbs/ae.
ow
BALANCE
0
332
154
72
6
6
2
0
b
Field
10575
5
Req'dNutrients
*134
0
140
0
0
0
0
0
p. Period
2.90
4/1-9/15
Supplied By_
CROP
Grain Sorghum, Silage
Starter
U
0
0
01
0
0
Commercial Fert.
{1
U
0
0
0
0
0
0
Soil Series
Nanford
Residual
0
0
0
0
0
0
0
0
ple Date
17.8 Tons
04-12-19
Manure
134
199
176
43
4
3
1
0
Rating
53 lbs/ac.
Low
BALANCE
0
199
36
43
4
3
l
()Field
E
10575
5
Req'dNutrients
93
0
80
0
0
0
0
0
p. Period
2.90
911-361
Supplied By:
CROP
Small Grain, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert,
0
0
0
0
0
0
0
0
Soil Series
Nanford
Residual
0
0
0
0
0
0
0
4
ple Date
8.6 Tons
04-12-19
Manure
93
22
236
11
U
0
0
0
Racing
46 lbs/ac.
Low
BALANCE
0
22
156
11
0
0
U
0
FApp.
Field
10575
6
Req'd Nutrients
193
110
20
0
0
0
0
0
Period
1.70
3/1-9/30
Supplied By:
CROP
Gammagrass Hay
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
61
0
0
0
0
0
0
Soil Series
Chewacla-CP
Residual
0
0
0
0
{1
0
0
0
RYE I Sample
Date
4.7 Tons
04-12-19
Manure
193
49
532
25
0
0
0
0
P Removal Rating
76 lbs/ac.
ow
BALANCE
0
0
512
25
0
0
0
U
NOTE: Symbol * means user entered data.
Preview Database Version 3.1 Date Printed: 4/1912019 NMR Page 5 of 7

Nutrient Management Recommendations Test
YEAR
2
N
(lbslA)
P205
(lbs/A)
K20
(ibs1A)
Mg
(lbs/A)
Mn
(lbs1A)
Zn
(lbs/A)
Cu
(lbs1A)
Lime
(tons/A)
Tract
r Field
10575
1
Req'd Nutrients
* 130
0
140
0
0
0
0
0
Acres App.
Period
21,30
4/1-9/15
Supplied By:
CROP
Crain Sorghum, Silage
Starter
0
0
0
0
0
00,
0
Commercial Fat.
0
0
0
0
0
0
0
0
Soil Series
Emporia
Residual
0
0
0
0
0
0
0
0
pleDate
*16.7Tons
04-12-19
Manure
130
30
329
15
0
0
0
0
Rating
50 lbs/ac.
Low
BALANCE
0
30
189
15
0
0
0
0
E
Field
10575
1
Req'dNutrients
*130
0
i40
0
0
0
0
0
p. Period
21.30
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
0
0
0
Commerci a] Fert.
a
0
0
0
0
0
o
0
Soil Series
Emporia
Residual
0
0
0
0
0
0
0
0
RYE Sample
Date
*16.7 Tons
04-12--19
Manure
130
30
329
15
0
0
0
0
P Removal
IRating
50 lbslac.
Low
BALANCE
0
30
119
15
0
0
0
0
Tract I Field
10575
2
Req'd Nutrients
172
0
140
0
0
0
U
0
Acres App. Period
15.10
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
U
0
0
CommercialFert.
0
0
0
0
0
0
0
0
Soil Series
Candor
Residual
(1
0
0
0
0
0
0
0
ple Date
*8.6 Tons
04-12-19
Manure
72
l7
l82
9
0
0
0
0
Rating
261bs/ac.
[.ow
BALANCE
0
J7
42
9
0
0
U
0
E
Field
10575
2
Req'dNutrients
*72
0
140
0
0
0
0
0
p. Period
15.10
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
U
0
0
01
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Candor
Residual
0
0
0
0
0
0
0
0
RYE I Sample
Date
*8.6 Tons
04-12-19
Manure
72
17
182
9
0
0
0
0
P Removal
Rating
26 lbslac.
Low
BALANCE
0
17
42
9
0
01
0
0
Tract
I Field
10575
4
Req'd Nutrients
137
0
140
0
0
0
0
0
Acres I App.
Period
1.00
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Nanford
Residual
0
0
0
0
0
0
0
0
RYE I Sample
Date
18.37ons
04-12-10
Manure
137
3i
377
18
0
0
0
0
m
P Reoval
Rating
55 lbslac.
Low
BALANCE
0
35
237
18
0
0
U
D
Preview Database Version 3.1 Date Printed: 4/19/2019 N1v1R Page 6 of 7

Nutrient Management Recommendations Test
YEAR
2
N
(lbs/A)
P205
(lbs/A)
K20
(lbs/A)
Mg
(lbs/A)
Mn
(lbs/A)
Al
(lbs/A)
Cu
(lbs/A)
Lime
(tonslA)
Tract
FFTeld
10575
4
Req'd Nutrients
137
0
140
0
0
0
0
0
Acres App.
Period
1.00
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
0
0
0
CommercialFert.
0
0
0
0
0
0
0
0
Soil Series
Nanford
Residual
0
0
0
0
0
0
0
0
RYE I Sample
Date
18.3 Tons
04-12-19
Manure
137
35
377
18
0
01
0
0
P Removal
Rating
55 lbs/ac.
Low
BALANCE
0
35
237
18
()
0
0
0
Tract
Field
10575
5
Req'd Nutrients
*134
0
140
0
0
0
0
0
Acres App.
Period
2.90
4/1-9/15
Supplied By --
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Nanford
Residual
0
0
1 0
0
0
0
0
0
RYE I Sample
Date
17.8 Tons
04-12-1.9
Manure
134
31
340
16
it
0
0
0
P Removal
Rating
53 lbs/ac,
Low
.BALANCE
0
31
200
16
0
0
0
0
Tract
Field
10575
5
Req'd Nutrients
* 134
0
140
0
0
0
0
0
Acres App.
Period
2.90
4/1-9/15
Supplied By:
CROP
Grain Sorghum, Silage
Starter
0
0
0
0
0
0
0
0
Commercial Fert.
0
0
0
0
0
0
0
0
Soil Series
Nanford
Residual
0
0
0
0
0
0
0
0
RYE I Sample
Date
17.8 Tons
04-12-19
Manurel
134
31
340
161
0
0
U
0
P Removal
Rating
53 lbs/ac.
Low
BALANCE
1 0
31
200
161
0
0
0
0
NOTE: Symbol * means user entered data.
Preview Database Version 3.1 Date Printed: 4/19/2019 NMR Page 7 of 7

0
b
0
N
0
0
0
0
o
O
o
0
0
0
0
0
o
a
o
0
0
0
0
0
0
0
Z
z
z
z
z
z
z
z
,z
z
z
z
z
Z
Z
Z
Z
z
z
z
7
Z
H
Nb
N
N
N
N
10
N
N
O
O
O
O
O
O
t
N
N
-
N
-
N
-
N
-
N
b
CD
V
O
V
O
-
0
a
0
0
0
0
0
0
0
0
a�
❑
0
U
C
0
C
o
C
a
C
a
C
a
C
o
0
0
0
0
C
0
0
0
C
0
C
0
z
2
Z
z
z
z
z
z
z
z
z
z
z
z
z
z
z
z
z
N
N
N
N
N
N
✓1
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N
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A

The following Lagoon Sludge Nitrogen Utilization table provides an estimate of the number of acres needed for
sludge utilization for the indicated accumulation period. These estimates are based on average nitrogen
concentrations for each source, the number of animals in the facility and the plant available nitrogen application
rates shown in the second column.
Lagoon sludge contains nutrients and organic matter remaining after treatment and application of the effluent. At
clean out, this material must be utilized for crop production and applied at agronomic rates. In most cases, the
priority nutrient is nitrogen but other nutrients including phosphorous, copper and zinc can also be limiting. Since
nutrient levels are generally very high, application of sludge must be carefully applied.
Sites must first be evaluated for their suitability for sludge application. Ideally, effluent sprayfields should not be
used for sludge application. If this is not possible, care should be taken not to load effluent application fields with
high amounts of copper and zinc so that additional effluent cannot be applied. On sites vulnerable to surface water
moving to streams and lakes, phosphorous is a concern. Soils containing very high phosphorous levels may also
be a concern.
Lagoon Sludge Nitrogen Utilization Table
Crop
Maximum
PA-N Rate
lblac
Maximum Sludge
Application Rate
1000 gal/ac
Minimum Acres
5 Years Accumulation
Minimum Acres
10 Years Accumulation
Minimum Acres
15 Years Accumulation
Swine Farrowing-Weanling Lagoon Sludge - Standard
Corn 120 bu
150
13.16
65.19
130.38
195.57
Hay 6 ton R.Y.E.
300
26.32
32.59
65.19
97.78
Soybean 40 bu
160
14.04
61.12
122.23
183.35
67157A Database Version 3.1 Date Printed: 04-16-2019 Sludge Page 1 of 1

The Available Waste Storage Capacity table provides all estimate of the number of days of storage
capacity available at the end of each month of the plan. Available storage capacity is calculated as the
design storage capacity in days minus the number of days of net storage volume accumulated. The start
date is a value entered by the user and is defined as the date prior to applying nutrients to the first crap in
the plan at which storage volume in the lagoon or holding pond is equal to zero.
Available storage capacity should be greater than or equal to zero and less than or equal to the design
storage capacity of the facility. If the available storage capacity is greater than the design storage
capacity, this indicates that the plan calls for the application of nutrients that have not yet accumulated.
If available storage capacity is negative, the estimated volume of accumulated waste exceeds the design
storage volume of the structure. Either of these situations indicates that the planned application interval
in the waste utilization plan is inconsistent with the structure's temporary storage capacity.
Avnilnble Waite Storage Cnnacity
Source Name
Farrow -to -wean morven
Design rage Capacity (Days)
Start Date
911
120
Plan Year
Month
Available Storage Capacity (Days)
1
1
44
1
2
16
1
3
28
1
4
120
1
5
89
1
6
59
1
7
98
1
8
120
1
9
90
1
10
59
1
11
111
1
12
80
2
1
49
2
2
21
2
3
33
2
4
23
2
5
54
2
6
24
2
7
120
2
8
89
2
9
59
2
10
28
2
11
74
2
12
43
* Available Storage Capacity is calculated as of the end of each month.
Preview Database Version 3.1 Date Printed: 04-16-2019 Capacity Page 1 of 1

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, historical
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, MRCS Field
Office Technical Guide Standard 393 - Filter Strips).
5. 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).
671. 74 Database Version 3.1 Date Printed: 4/16/2019 specirication Page 1

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.
10. 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 Iand 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 that 25 feet to perennial waters.
12. Animal waste shall not be applied closer than 100 feet to wells.
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.
671574 Database versioxa 3. 1 Date Printed: 411612019 Spcciircatioii Page 2

15. AnimaI waste shall not be discharged into surface waters, drainageways,
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 washdown 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.
20. 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.
671574 Database Version 3.1 Date Printed: 4I16I2019 Specitwatton Fage 3

22. Waste shall be tgte within 60 days of utilization and soil shall be tested
at least � at cr`sles 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.
671.574 Database Version 3.1
Date Printed_ 4/16/2019 Specification Page 4

NUTRIENT MANAGEMENT and
WASTE UTILIZATION PLAN
SUPPLEMENTAL INFORMATION
N.C. Practice Job Sheet: NC-590-633
Prepared for: 1A) k 16 Roc-k FGrrY, s j w i ne Y140AN" —
In
Farm:
WHAT IS NUTRIENT MANAGEMENT?
The conservation practice, Nutrient
Management, is managing the amount,
source, placement, form and timing of the
application of nutrients and soil amendments
to achieve realistic production goals, while
minimizing nutrient movement to surface or
ground waters. The practice, Waste
Utilization, is using agricultural waste such as
manure or wastewater in an environmentally
sound manner. These practices are jointly
accomplished through the development of a
Nutrient Management/Waste Utilization Plan,
which is normally part of a broader
Conservation Plan that addresses multiple
natural resource concerns on the land.
PURPOSE OF NUTRIENT MANAGEMENT
and WASTE UTILIZATION PRACTICES
Your nutrient management/waste utilization
plan is intended to accomplish one or more of
the following objectives:
• To budget nutrients for plant production.
• To properly utilize manure or organic by-
products as a plant nutrient source.
• To minimize the delivery of agricultural
nutrients to surface and ground water
resources.
+ To maintain or improve the physical,
chemical, and biological condition of the
soil.
Tract: Date:J_��
To utilize agricultural wastes for
livestock feed or as an energy source.
CONTENTS OF THE NUTRIENT
MANAGEMENT ! WASTE UTILIZATION
PLAN
The information provided in this Job
Sheet and the attachments meet the
minimum requirements for a Nutrient
Management Plan for USDA-NRCS
purposes. This Nutrient Management
Plan includes:
1 A plan map and soils map for the area
planned (these may be part of the
overall Conservation Plan).
2. Location of designated sensitive areas
or resources (streams, wells,
sinkholes, etc.) and any associated
nutrient application setbacks, etc.
3. Your planned crop rotation.
4. Results of soil, plant, water tests.
5. Results from Phosphorus Loss
Assessment Tool (PLAT) or Leaching
Index (LI) as required.
6. Realistic yield expectations for the
crops in the rotation, and their source
if other than default values approved
for N.C.
7. Recommended nutrient application
rates for nitrogen, phosphorus, and
potassium, as well as timing, form,
NC Practice Job Sheet: NC-590 (August, 2003) Page 1

and method of application and
incorporation, if applicable.
8. This Job Sheet (or comparable
information), that provides the following:
• General requirements of this practice,
as well as additional requirements to
meet the natural resource protection
purposes listed above.
Additional considerations specific to
this plan.
• Operation and maintenance
information associated with this
practice.
Because this Nutrient Management Plan
includes agricultural organic sources,
additional items are required in the plan to
ensure proper waste utilization:
• Waste Utilization Agreement (if
applicable)
• Waste Utilization Third Party
Agreement (if applicable)
• Additional engineering design and
operating information for waste storage
structures, transport, and application
system, as applicable. These designs,
and the instructions for operating these
structures, is an integral component of
your overall Nutrient Management/
Waste Utilization Plan.
• Emergency Action Plan to prevent
overtopping or other discharges from
storage structures or facilities, as
applicable.
This plan was developed based on the current
NRCS 590 and 633 standards and Federal,
state, or local regulations or policies.
Changes in laws or regulations may
necessitate a revision of the plan.
BASIC REQUIREMENTS FOR WASTE
UTILIZATION
General
All manure and organic residues must be
applied according to a nutrient management
plan (see the following section, "BASIC
REQUIREMENTS FOR NUTRIENT
MANAGEMENT")
You are required to acquire and comply
with all federal, state, or local permit
requirements related to the handling and
application of manure or organic
materials.
The nutrient management/waste
utilization plan must address all organic
waste generated at or brought to the
facility. A Waste Utilization Third Party
Agreement must exist to address all
organic waste not handled by the nutrient
management/waste utilization plan.
Manure or organic wastes will not be
applied to the following areas:
• surface waters,
• wetlands, unless constructed as a
component in a waste treatment
system,
• soils subject to frequent flooding
during the period when flooding is
expected,
• frozen, snow-covered, or saturated
soils,
• within 200 feet of a dwelling other
than those owned by the producer,
• within 100 feet of a well,
• within 25 feet of surface waters, or
• within any other setbacks as identified
by federal, state, or local laws or
regulations (e.g. NC General Statute
prevents swine lagoon effluent from
being applied within 75 feet of a
residential property boundary or
perennial stream or river if the facility
was sited on or after October 1995.)
Manure or organic wastes will be applied
in a manner not to reach surface waters,
wetlands (unless constructed as a
component in a waste treatment system),
property owned by others, or public right-
of-way.
Sludge that accumulates in waste storage
structures must be analyzed prior to land
NC Practice Job Sheet: NC-590 (August, 2003) Page 2

application. Adequate provisions (available
land and/or third party manure agreements)
must exist to ensure sludge is applied in
adherence to all nutrient application
requirements. All federal and state guidance
regarding the proper testing, handling,
planning, and application of sludge must be
followed for regulated operations.
Since compliance with all applicable North
Carolina laws is the responsibility of the
producer, you should consult the most current
version of the Guidance Memo for
Implementing the Environmental Management
Commission's Regulations for Animal Waste
Management for questions.
ADDITIONAL REQUIREMENTS FOR
PROVIDING LIVESTOCK FEED
If applicable, all agricultural wastes or other
organic residues used for feedstock must be
handled in a manner to minimize
contamination and preserve its feed value.
Chicken litter stored for this purpose must be
covered. A qualified animal nutritionist shall
develop rations that utilize animal wastes.
ADDITIONAL REQUIREMENTS FOR
PROVIDING A SOURCE OF ENERGY
if your facility is to be used for energy
production, all energy producing components
of the system are included in the Nutrient
Management/Waste Utilization Plan and
provisions for the utilization of residues of
energy production identified. Your Nutrient
Management Plan includes the use of these
residues, if applicable.
BASIC REQUIREMENTS FOR NUTRIENT
MANAGEMENT
General
Application of nutrients must comply with all
applicable Federal, state, and local laws and
regulations.
The realistic yield expectations (RYES) in
this plan are based on one or more of the
following:
• Default values approved by the N.C.
Interagency Nutrient Management
Committee that incorporate soil
productivity information, yield data,
and research with North Carolina
soils, and cropping systems.
Additional information on the default
values may be found at:
www.soil.ncsu.edulnmp nncnmw.glindex,hfm
Documented actual yield data from
the site, determined by the average of
the highest three yields of the last five
consecutive specific crop harvests.
(For forage crops, determine the
average of the highest three years of
the last five years.)
A fertilization rate recommended by
North Carolina State University may
be used in cases where no yield data
or approved RYE values exist for a
crop.
• An RYE inferred from a similar crop
on a soil with similar physical and
chemical features may be used for
new crops or in the absence of other
RYE data. This inferred RYE may
ONLY be specified by a certified
Nutrient Management planner.
Erosion, runoff, and water management
controls have been planned, as needed,
on fields that receive nutrients.
Soil Testing
This nutrient management plan has been
developed based on current soil test
results (no older than three years).
Soil samples must be collected and
prepared in accordance with North
Carolina State University or the North
Carolina Department of Agriculture and
Consumer Services (NCDA&CS)
Agronomic Division standards or
recommendations.
NC Practice Job Sheet: NC-590 (August, 2003) Page 3

Soil test analyses can be performed by any
laboratory or program that is certified by the
North Carolina Department of Environment
and Natural Resources (NCDENR), Division of
Water Quality, Laboratory Section.
NCDA&CS Agronomic Division uses the
Mehlich-3 extractant process for soil testing.
Growers who utilize other laboratories must
request the use of the Mehlich-3 methodology
to ensure the test results are compatible with
North Carolina's nutrient management
planning and assessment tools. For statewide
consistency, all laboratories used must
provide fertilization recommendations using
guidelines and methodologies as referenced
at the NCDA&CS website:
www. ngagr. com/aaronomt/nbook _htm
Growers are encouraged to use a laboratory
that is supported by field research within the
state.
Soil testing shall include analysis for all
nutrients for which specific information is
needed to develop the nutrient plan.
Plant Tissue Testing
Tissue sampling and testing, when used, shall
be done in accordance with North Carolina
State University or NCDA&CS standards or
recommendations.
Manure Testing
Nutrient values of manure and organic by-
products shall be established for planning
purposes based on laboratory analysis,
acceptable default values, or historic records
for the operation.
When determining actual application rates, a
laboratory analysis is required. State
regulations require that waste be tested within
60 days of utilization for some operations. In
the case of daily spreading, the waste must be
sampled and analyzed at least once a year.
Acceptable laboratories include the
NCDA&CS Agronomic Division, or others
certified by the NCDENR.
Field Risk Assessment
A field -specific assessment of the
potential for phosphorus transport from
each field (or groups of similar fields)
have been conducted, using the North
Carolina Phosphorus Loss Assessment
Tool (PLAT)
PLAT assesses the potential for
phosphorus (P) to be transported from the
site to surface water through each of the
four primary loss pathways:
• sediment -bound P transported
through erosion,
• soluble P transported through
surface runoff,
• soluble P leached through the soil
profile, and
• non -incorporated source P
transported through surface
runoff.
Based on the assessment of each loss
pathway, PLAT produces a single rating
for each field. As shown below, this
rating will identify whether nitrogen or
phosphorus shall be the rate -determining
element in developing the planned
application rate for manure.
PLAT Rating
I Nutrient Application Criteria
LOW
Nitrogen -based manure
a lication.
MEDIUM
Nitrogen -based manure
application,
HIGH
Manure application limited to
phosphorus removal from site
in harvested plant biomass.
VERY HIGH
No additional manure
application to be specified in
plan for the site.
On all sites, regardless of the PLAT
rating, starter fertilizers may be
recommended in accordance with NCSU
guidelines or recommendations.
NC Practice Job Sheet: NC-590 (August, 2003) Page 4

In some cases, specific conservation practices
that reduce the potential for phosphorus
transport have been incorporated into PLAT.
Examples include buffers or filter strips,
ponds, water table management, and residue
management and conservation tillage.
Similarly, soil erosion rates, either existing or
planned, have been incorporated into your
PLAT analysis. This information is shown on
the PLAT results enclosed. Because the
management of the site actually affects the
PLAT rating, all practices identified on the
PLAT analysis (including any required to
achieve the specified erosion rate) must be
either already installed or included in a
Conservation Plan for the Nutrient
Management Plan to be approved.
Nutrient Application Rates
Recommended nutrient application rates are
based on North Carolina State University or
NCDA&CS recommendations that consider
current soil test results, RYES, and
management.
Liming material shall be applied as needed to
adjust soil pH to the specific range required by
the crop or crops in the rotation for optimum
availability and utilization of nutrients.
The application amount and rate (in/hr) for
liquid wastes (e.g. applied through irrigation)
shall not result in runoff from the site. The
application shall not exceed the field capacity
of the soil.
The planned rates of nutrient application are
shown on the attached sheets. These rates
have been computed as follows:
Nitrogen Application - When the plan is
nitrogen -based (a PLAT rating of Low or
Medium), the application rate of manure or
organic by-products shall be based on the
recommended nitrogen rate using the RYE
for the site (or a rate recommended by
NCSU or NCDA in the case of crops
without established RYES). This may
result in an application rate for other
nutrients that exceeds the soil test
recommendation.
When the plan is being implemented
on a phosphorus standard (a PLAT
rating of High or Very High), manure
or other organic by-products shall be
applied at rates consistent with the
phosphorus application guidance
below. In such situations, an
additional nitrogen application from
non -organic .sources may be required
to supply nitrogen at the rate
recommended by the RYE.
• Within the limits allowed by PLAT,
manure or other organic by-products
may be applied on soybeans at rates
equal to the estimated removal of
nitrogen in harvested plant biomass.
All nitrogen rates for hay production
are for pure grass stands. Due to the
nutrient recycling by grazing animals,
the planned nitrogen rate per unit
yield for hay crops shall be reduced
by 25% for the portion of the expected
yield that is removed through grazing.
Phosphorus Application — When
manure or other organic by-products
are used, the planned rates of
phosphorus application shall be based
on the PLAT rating for the site, as
follows:
Low or Medium Rating — The
planned manure or organic by-
product application rate is based
on the nitrogen needs of the crop.
High Rating — The planned
manure or organic by-product
application rate is limited to the
phosphorus removal rate of the
harvested plant biomass.
Very High Rating — No additional
manure or organic by-product
application is specified in the plan.
NC Practice Job Sheet: NC-590 (August, 2003) Page 5

On all sites, regardless of the PLAT rating,
starter fertilizers containing nitrogen,
phosphorus, and potassium may be
recommended in accordance with North
Carolina State University guidelines or
recommendations.
A single application of phosphorus applied
as manure or organic by-product may be
made at a rate equal to the recommended
phosphorus application or estimated
phosphorus removal in harvested plant
biomass for the crop rotation or multiple
years in the crop sequence.
• When such single applications are
made, the rate shall:
♦ not exceed the recommended
nitrogen application rate during the
year of application, or
♦ not exceed the estimated nitrogen
removal in harvested plant bio-
mass during the year of application
when there is no recommended
nitrogen application, or
♦ not be made on sites with a Very
High PLAT risk rating.
• Potassium Application — Planned
potassium application rates should
match the soil test recommended rates
as closely as possible. (This is
Particularly critical in situations where a
potentially harmful nutrient imbalance
in crops or forages may occur, such as
grass tetany). When using manure or
other organic sources, the addition of
potassium from non -organic sources
may be required.
• Other Plant Nutrients - The planned
rates of application of other nutrients if
applicable are consistent with North
Carolina State University or the
NCDA&CS guidelines or
recommendations.
Nutrient Application Timing
Timing of nutrient application shall
correspond as closely as possible with
plant nutrient uptake characteristics, while
considering cropping system limitations,
weather and climatic conditions, and field
accessibility. Nutrients shall not be
applied to frozen, snow-covered, or
saturated soil.
Manure or organic by-products shall not
be applied more than 30 days prior to
planting of the crop or forages breaking
dormancy.
For nutrients applied through irrigation
systems, application equipment should be
properly calibrated to ensure uniform
distribution of material at planned rates.
Plan Review and Revision Period
A thorough review and revision (if
needed) of the nutrient management plan
shall be conducted on a regular cycle, not
to exceed five years.
Heavy Metals Monitoring
For animal waste, including sludge, zinc
and copper concentrations shall be
monitored and alternative crop sites for
application shall be sought when these
metals approach excessive
concentrations. The following criteria and
actions are provided:
ZINC
Mehlich-3lndex
�-
Action
Zn-I
300 (21 Ibs/ac)
Peanuts are very sensitive to
zinc, and application on peanuts
should be limited. Seek
alternative sites when possible.
The risk of zinc toxicity is
greater with low soil pH and has
been seen at Zn-I as low as
300. `
500 (35 Ibsfac)
Critical toxic level for peanuts.
Cease application on peanuts.'
2,000 (142
Caution: Seek alternative sites
Ibs/ac)
when possible for all crops.
3,000 (213
Critical toxic level for all crops.
NC Practice Job Sheet: NC-596 (August, 2003) Page 6

Mehlich-3Index Action
(Cu-I1
2,000 (72 Ibslac) Caution: Seek alternative sites
when possible for all crops. *
3,000 (108 Critical toxic level for all crops.
lbslac) Cease application on all crops.
* Maintain pH at 6.0 on these
sites.
When sewage sludge is applied, the
accumulation of potential pollutants (including
arsenic, cadmium, copper, lead, selenium,
and zinc) in the soil shall be monitored in
accordance with the US Code, Reference 40
CFR, Parts 403 and 503, and applicable state
and local laws or regulations. Additional
information on heavy metal criteria for sewage
sludge may be found in Land Application of
Sewage Sludge, E;PA1831-B-93-002b
publication number at:
h ttp://www. epa.gov/npdes/,vub"ludge.,odf
ADDITIONAL REQUIREMENTS FOR
MINIMIZING DELIVERY OF NUTRIENTS TO
SURFACE AND GROUND WATER
In areas that have been identified as impaired
with agricultural nutrients being a likely
source, an assessment shall be completed of
the potential for nitrogen or phosphorus
transport from the site. (The streamstwater
bodies in this category are listed in the USDA-
N RCS Field Office Technical Guide, Section
1.1
❑ NO
This nutrient management plan IS NOT in
an area where surface waters are
impaired, with agricultural nutrients
identified as a likely source. The Leaching
Index (LI) is not required.
❑ YES
This nutrient management plan IS in an
area where surface waters are impaired,
with agricultural nutrients identified as a
likely source. The Leaching Index (LI)
is included in this plan.
While the results of the LI does not affect
your planned nutrient application rates,
some additional conservation practices
may be specified in the plan to reduce the
risk of nutrient movement from the field, if
applicable.
IMPORTANCE OF MANAGING
NUTRIENTS
Nitrogen and phosphorus are water
soluble elements and either or both may
be components of organic and inorganic
fertilizers. In soluble forms, both can
move with water as leachate down
through the soil, or over the soil surface
as runoff after rainfall. While nitrogen and
phosphorus exist in different forms and
may move through different transport
processes on the same site, they both
can have detrimental effects on both
surface and shallow ground water quality.
As an example, excess nutrients can
result in accelerated eutrophication with
severe algal blooms and fish kills.
Because of the topography, hydrology,
and other factors in the state, the
environmental problems from excess
nutrients reaching surface water may not
be exhibited near the contributing source,
but rather create water quality problems
far downstream. Consequently, the
Neuse River Basin, Tar -Pamlico Basin,
the Chowan River, the watershed of the
B. Everett Jordan Reservoir, and the
watershed of the New River in Onslow
County are listed as Nutrient Sensitive
waters in North Carolina.
Nitrogen: Nitrogen applied as fertilizer or
organic material is transformed into
nitrate and can move with the water
moving downward into the shallow ground
water and eventually to surface waters.
(Relatively small amounts of nitrogen
reach our surface waters through rainfall
runoff. ) The Leaching Index (LI) is a
NC Practice Job Sheet: NC-590 (August, 2003) page 7

required park of the nutrient management plan
in some areas of the state with surface water
impairments. The LI uses soils information
and local climate data to assess the potential
hazard from leaching of nutrients. The results
of the Ll analysis and recommended actions
are included in your nutrient management
plan, if applicable.
Phosphorus: Research in recent decades
indicates that, with high soil phosphorus
levels, phosphorus has more potential to be
transported off -site than recognized in the
past. Phosphorus can be transported in
several ways: (1) attached to soil particles
leaving the field through erosion, (2) in soluble
form leaving the field in surface runoff, and (3)
in soluble form leaching downward through
the soil profile, and eventually into surface
water. Unlike nitrogen, the most likely
transport pathway for phosphorus varies by
site, and depends upon such factors as soil
erosion rate, soil phosphorus levels, texture of
soils, existence of buffers, and other factors.
In N.C., PLAT is the tool used to assess
potential excessive phosphorus losses. The
results of the PLAT analysis and
recommended actions are included in your
nutrient management plan, if applicable.
If a site receives a PLAT rating of Low or
Medium, then applying manure at rates based
on the nitrogen needs of the crop is allowed.
It is important to realize that this may result in
phosphorus being applied at rates that
significantly exceed the crop's phosphorus
removal rate. In these cases, the planned
nutrient application rate is not sustainable,
and eventually a PLAT rating of High may be
reached.
OPERATION & MAINTENANCE
You are responsible for safe operation and
maintenance of this practice, including all
equipment. The following Operation &
Maintenance should be conducted:
1 Review the plan annually to determine if
adjustments or modifications to the plan
are needed. (The S.B. 1217
interagency group guidelines
accepted by the N.C. Division of
Water Quality for .0200 operations
specify a plan revision when there are
changes in crops or cropping patterns
that utilize more than 25 percent of
the nitrogen generated by the
operation.) As a minimum, nutrient
management plans shall be
thoroughly reviewed every five years
and revised if necessary. The next
review will Pe performed in
yv Z
2. Protect fertilizer and organic by-
product storage facilities from weather
and accidental leakage or spillage.
3. Ensure proper calibration of
application equipment to ensure
uniform distribution of material at
planned rates.
4. Inspect and maintain the equipment
and facilities used to implement the
Nutrient Management/Waste
Utilization Plan regularly. Any needed
repairs should be made in a timely
manner.
5. Review the Emergency Action Plan, if
applicable, annually.
6. Records should be maintained for five
years, or for a period as required by
other Federal, state, or local
ordinances, or program or contract
requirements. To ensure adequate
information exists to support sound
nutrient management, NRCS
recommends the following records be
included:
• Soil test results and
recommendations for nutrient
application,
• Quantities, analyses and sources
of nutrients applied (When the
actual rates used exceed the
recommended and planned rates
on inorganic fertilizer plans,
NC Practice Job Sheet: NC-590 (August, 2003) Page 8

records should indicate the reasons for
the differences, e.g. inability to acquire
custom blended fertilizer.)
E• Dates and method of nutrient
applications,
• Crops planted, planting and harvest
dates, yields, and crop residues
removed,
• Results of water, plant, and organic by-
product analyses, and
+ Dates of review and person performing
the review, and recommendations that
resulted from the review.
NOTE: State laws or regulations may
define record -keeping requirements for
some operations.
7. Ensure that workers are protected from
and avoid unnecessary contact with
inorganic fertilizers and organic by-
products. Protection should include the
use of protective clothing when working
with plant nutrients. Extra caution must be
taken when handling ammonia sources of
nutrients, or when dealing with organic
wastes stored in poorly ventilated
enclosures.
8. Properly dispose of material generated by
the cleaning of nutrient application
equipment. 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.
9. Properly dispose of or recycle nutrient
containers according to state and local
guidelines or regulations.
NC Practice Job Sheet: NC-590 (August, 2003) Page 9

Crop Notes
Corn Silage - medium leaching
Corn Silage - high leaching
The following crop note applies to field(s): 1
The following crop note applies to field(s): 2
The following crop note applies to field(s): 4, 5
Corn Silage: Piedmont and Mountains
In the Piedmont, corn should be planted when soil temperature reaches 52 to 55 degrees fahrenheit. Plant
1-2" deep. Adequate depth control is essential. Review the NCSU Official Variety "green book" and
information from private companies to select a high yielding variety with the characteristics needed for
your area and conditions. Apply 10 to 12 lbs. nitrogen per ton of expected yield. All nitrogen can be
applied at planting. Also acceptable is to apply 2/3 to 3/4 of the nitrogen at planting and the rest when
corn is in the 7 to 9 leaf stage. Tropical corn for silage needs about 6-8 lbs nitrogen per ton of expected
yield applying no more than 100 to 120 lbs total nitrogen. Research has shown that nitrogen can be
reduced by approximately 15 percent when soil injected. The total N is dependent on the soil type and
expected yield. Apply phosphorus and potassium according to a soil test before planting. Phosphorus
is best utilized when banded with the planter as a starter. Plant samples can be analyzed during the
growing season to monitor the nutrient status of the corn. Timely management of weeds and insects is
essential in profitable corn silage production. Plant a cover crop after harvest.
The following crop note applies to field(s): 1
Small Grain Silage
The following crop note applies to field(s): 2
Small Grain Silage
671374 Database Version 3.1 Date Printed: 04-16-2019 Crop Note Page 1 of 3

The following crop note applies to field(s): 4, 5
Small Grain Silage, Piedmont and Mountains
In the Piedmont, small grain silage should be planted from October 10 to November 3. In the Mountains,
small grain silage should be planted from September 15 to October 31. Plant 18 to 22 seed/drill row foot
at 1-1 1/2" deep and increase the seeding rate by 5% for each week seeding is delayed beyond the
optimum time frame. See the seeding rates table for applicable seeding rate modifications in the current
NCSU "Small Grain Production Guide".Also, increase the initial seeding rate by at least 10% when
planting no -till. Adequate depth control when planting the small grain is essential. Review the NCSU
Official Variety "green book" and information from private companies to select a high yielding variety
with the characteristics needed for your area and conditions. Apply approximately 30 lbs N at planting.
Increase N at planting by 20% for no -till. Phosphorus and potassium should be applied according to a
soil test at this time. The remaining N should be applied during February -March. Apply 10 to 12 lbs. N
per ton of expected yield. The total N is dependent on soil type and expected yield. Plant samples can be
analyzed during the growing season to monitor the nutrient status of the small grain. Timely management
of diseases, weeds and insects are essential for profitable small grain silage production. Plant a cover
crop after harvest.
The following crop note applies to field(s): 1
Sorghum and sorghum/sudan hybrids planted for silage are normally planted from May 15 to July 15 in
the Piedmont and Mountains. They can be a good substitute for late planted corn and are more drought
tolerant. Review data available to select a variety with the characteristics needed for your area. Planting
rates are usually 9 to 12 pounds per acre planted and 20 to 25 pounds drilled. See recommended planting
rate on bag for best results per variety. Apply phosphorus and potassium recommended by a soil test
before planting. A nitrogen rate of 100 to 120 pounds of nitrogen is sufficient for crop growth. Nitrogen
should be applied at 7-9 pounds per ton of expected yield. The total amount of nitrogen is dependent on
soil type. Plant samples can be analyzed during the growing season to monitor the nutrient status of the
sorghum. Timely management of weeds is essential. You will need to get protected seed before some
herbicides can be used. Check with your local extension agent for herbicides and seed treatments
necessary before planting. Plant a cover crop after you harvest silage.
The following crop note applies to field(s)_ 2
Sorghum and sorghum/sedan hybrids planted for silage are normally planted from May 15 to July 15 in
the Piedmont and Mountains. They can be a good substitute for late planted corn and are more drought
tolerant. Review data available to select a variety with the characteristics needed for your area. Planting
rates are usually 9 to 12 pounds per acre planted and 20 to 25 pounds drilled. See recommended planting
rate on bag for best results per variety. Apply phosphorus and potassium recommended by a soil test
before planting. A nitrogen rate of 100 to 120 pounds of nitrogen is sufficient for crop growth. Nitrogen
should be applied at 7-9 pounds per ton of expected yield. The total amount of nitrogen is dependent on
soil type_ Plant samples can be analyzed during the growing season to monitor the nutrient status of the
sorghum. Timely management of weeds is essential. You will need to get protected seed before some
herbicides can be used. Check with your local extension agent for herbicides and seed treatments
necessary before planting. Plant a cover crop after you harvest silage.
671574 Database Version 3.1 Date Printed: 04-16-2019 Crop Note Page 2 of 3

The following crop note applies to field(s): 4, 5
Sorghum and sorghum/sudan hybrids planted for silage are normally planted from May 15 to July 15 in
the Piedmont and Mountains. They can be a good substitute for late planted corn and are more drought
tolerant. Review data available to select a variety with the characteristics needed for your area. Planting
rates are usually 9 to 12 pounds per acre planted and 20 to 25 pounds drilled. See recommended planting
rate on bag for best results per variety. Apply phosphorus and potassium recommended by a soil test
before planting. A nitrogen rate of 100 to 120 pounds of nitrogen is sufficient for crop growth. Nitrogen
should be applied at 7-9 pounds per ton of expected yield. The total amount of nitrogen is dependent on
soil type. Plant samples can be analyzed during the growing season to monitor the nutrient status of the
sorghum. Timely management of weeds is essential. You will need to get protected seed before some
herbicides can be used. Check with your local extension agent for herbicides and seed treatments
necessary before planting. PIant a cover crop after you harvest silage.
The following crop note applies to field(s): 3, 6
Eastern Gamagrass: No Comment.
671574 Database Version 3.1 Date Printed: 04-16-2019 Crop Note Page 3 of 3

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