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Steve Troxler North Carolina Department of Agriculture David Williams
Commissioner and Consumer Services Director
Division of Soil and Water Conservation
Environmental Services Section, Soil Interpretive Services
Soils & Water Table Elevation Investigation Report
Report Date: November 3, 2023
Date of Investigation: November 1, 2023
Project: AFO Lagoon Closure -Amick Farm
Obiective of Soils Investigation: To characterize soils and establish the depth to water table in
the area of the existing lagoon as part of a lagoon closure project.
Soil Scientist: Patrick Mitchell, LSS—NCDSWC
Others Present: Michael Shepherd—NCDSWC; and Grayson Sarif—USDA-NRCS.
Location: The site is located near address#760 Sides Rd., Albemarle,NC.
GPS Coordinates: 35.281, -80.2468. See the attached soils map for the areas investigated.
Geology/Parent Material: The site is located within the Carolina Slate Belt Soil System of the
NC Piedmont. The parent materials consist of alluvium from slates, siltstones, and sandstones.
Topography/Soils: The lagoon is situated adjacent to the floodplain on Long Creek. The NRCS
Soil Survey shows the area primarily mapped as Oakboro silt loam, 0 to 2% slopes (OaA), and
Chenneby silt loam, 0 to 2% (CfA); with minor inclusions of other soils in each area.
The onsite soils investigation indicates that the Oakboro soil series and Shellbluff soil series
predominate the areas immediately adjacent to the toe of the lagoon embankment.
Field Work: A total of eight hand auger borings were advanced to characterize soils and to
determine the depth to water table. No soil borings were placed in the floor of the lagoon due to
the liquid levels present in the lagoon bottom. The north end of the lagoon was not investigated
due to the large depth of existing fill material in place. Auger borings were placed immediately
adjacent to the toe of the lagoon embankment, in natural ground. The locations of soil borings can
be found on the attached map.
Results and Recommendations: The investigation found that most of the soils surrounding the
lagoon have the presence of a seasonal high water table (SHWT). The depths to SHWT were
determined based upon soil morphological characteristics described for each soil profile. The
presence of redoximorphic features (i.e., reduction and oxidation) was used to make
determinations. This was accomplished by identifying soil mottling (depletions and
concentrations) utilizing a Munsell soil color book. The presence of depletions with a color of

Chroma 2 or less, and 2%or greater in occurrence indicate extended saturated conditions required
to be determined as a water table. All soil borings were found to be dry at the time of investigation
(i.e., no apparent water table—no saturated soils, no free water).
An elevation survey was completed at the site. Elevation measurements were made at the grounds
surface at each auger boring location and at the top of the dam. These elevations were used with
the respective depths to SHWT for each auger boring to determine the elevation of the SHWT.
Table 1. below shows the elevations of the water table for each auger boring in relation to the
elevation of the lagoon bottom. The lagoon bottom elevation was provided in the as-built drawing
for the lagoon from the facility files.
Water Lagoon
Auger Table Bottom
Boring ID Elevation Elevation
1 34.88
2 33.88
3 33.29
4 33.88 38.00
5 35.35
6 35.29
7 34.10
8 35.84
Table 1. Water Table Elevations vs Lagoon Bottom Elevation.
The elevations shown in the table above suggests that the bottom of the lagoon is above the SHWT.
For questions or comments, contact Patrick Mitchell at 919-280-4332 or at email:
patrick.mitchell(c ncagr`gov.
G �5 G��. M/ �2
Patrick L. Mitchell LSS <G N ,,STA 'y
Regional Soil ScientistL�
NC Division of Soil and Water Conservation �-
a
'!Oun�F
Attachments: � 1312 �Qv
Soils—SHWT Elevations Map O P.
RTH G
2

RERERENCES:
Daniels, R.B., Buol, S. W., Kleiss, H.J., Ditzler, C.A. 1999. Soil Systems in North Carolina, Technical
Bulletin 314. North Carolina State University, Soil Science Department. Raleigh,North Carolina 27695-
7619.
Natural Resources Conservation Service, National Soil Survey Center. 2012. Field Book for Describing
and Sampling Soils. United States Department of Agriculture. Lincoln,Nebraska.
North Carolina Agricultural Research Service. 1992. Redoximorphic Features for Identifying Aquic
Conditions. North Carolina State University Technical Bulletin 301. 33 pages.
Soil Survey Division Staff. 1993. Soil survey manual. Soil Conservation Service. U.S. Department of
Agriculture Handbook 18. (Last modified March 28, 2011).
https:llwebsoilsurvey.sc.egov.usda.govIAppIWebSoilSurvey.aspx, retrieved 11/02/2023.
Soil Survey Staff. 2014. Keys to Soil Taxonomy, Twelfth Edition. Natural Resources Conservation Service.
U.S. Department of Agriculture.
3

J-Caine Inc
4/18/2023
This plan has been prepared for: This plan has been developed by:
J-Caine Inc NRCS
Josh Amick Grayson Sarif
PO BOX 515 26032-C Newt Rd
Norwood, NC 28128 Albemarle, NC 28001
704-961-2846 704-441-4029
Devej6per natu
Type of Plan: Nutrient Management with os a Clea 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.
Signature(owner) Date
29
I L
Signatur ( nager 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.
Digitally signed by LEE
LEE HHOLCOMB
H O LC O M B Date:2023.08.16
Plan Approved By: 14:17:32-04'00'
Technical Specialist Signature Date

Waste Storage Closure Source Description
J-Caine Inc
SOURCE: Liquid for Mixing
Date Measured: 04/18/2023
Lagoon Dimensions: TOP-459 X 944; BOTTOM-415 X 900;SIDE SLOPES-2:1
Liquid Depth:7.00 ft.; Liquid Volume: 11,600,000 gallons. Waste Sample M FY23-
W004225
Sludge Depth:4.00 ft.: Sludge Volume:8,000,000 gallons. Waste Sample#: Fy18-
W003699
U 1003 Liquid for Mixing is an animal waste storage structure that is no longer in operation and is being closed as part
of a closure plan.There are an estimated 19,600,000 gals in this structure prior to closure.
Estimated Plant Available Nitrogen
Application Method (Ibs N/1000 gals) Source Total(Ibs)
Injected 1.77 34,720
Incorporated-4 wks or less following 1.77 34,720
application
Incorporated-5 wks to 3 mos 1.48 28,933
following application
Broadcast 1.48 28,933
Irrigated 1.48 28.933
Max.Available PAN(Ibs) Actual PAN Applied(Ibs) PAN Surplus/Deficit(Ibs) Actual Volume Applied Volume Surplus/Deficit
(Gallons) (Gallons)
28.933 35,794 (6,861) 24,247,561 (4,647,561)
Note: In Source ID,S means standard source,U means user defined source.
Maximum PAN Available is calculated on the basis of the actual application method(s)identified in the plan for this source.
8/7/2023 12:58:52 PM 1/1

Sources in Plan
J-Caine Inc
Nutrients applied in accordance with this plan will be supplied from the following
source(s):
Commercial Fertilizer is included in this plan.
U 1003 Liquid for Mixing waste generated 19,600,000 gals/year by a 0 Poultry Lagoon Liquid-Layer
operation.This production facility has waste storage capacities of approximately 0 days.
Estimated Pounds of Plant Available Nitrogen Generated per Year
Injected 34,720
Incorporated-4 wks or less 34,720
following application
Incorporated-5 wks to 3 mos 28,933
following application
Broadcast 28,933
Irrigated 28,933
Max.Available Actual PAN PAN Surplus/ Actual Volume Volume Surplus/Deficit
PAN(Ibs) Applied(Ibs) Deficit(Ibs) Applied(Gallons) (Gallons)
Year 1 t 28.933 35,794 (6,861) 24.247,661 (4,647,561)
8/7/2023 12:58:16 PM 1/1

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J-Caine Inc
4/18/2023
Type of Plan: Nutrient Management with Closure Cleanout Only
Narrative:
This plan is for the closure of the 9ac lagoon owned by J-Caine Inc.The lagoon has a current
volume of 11.6 million gallons of liquid and 8 million gallons of sludge. 19.6 million gallons total.The
lagoon will be agitated and land applied by both a private contractor and the landowner.All solids
will be removed and dam will be breached upon completion.All liquid will be land applied at soil
infiltration rates due to minimal lagoon liquid nutrient content,All liquid will be applied on 596.9 ac
identified In this plan.This plan includes 546.9 ac of cropland and 50 ac of pasture. Required
buffers were taken into account when determining wettable acres.
8/7/2023 1:00:06 PM 1/1

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Required Soil Test Values
J-Caine Inc
The Required Soil Test Values shown in the following table provide a summary of recommended actions that
should be taken based off information provided at time of soil tests.Fields that receive manure must have a soil
analysis conducted at least once every three years. High levels of zinc and copper can adversely affect plant
growth.Alternative crop sites must be used when the concentration of these metals approach excessive levels.
Site life can be estimated by dividing the amount of copper and zinc to be applied in Ibs/acre by 0.036 and 0.071,
respectively and multiplying the result by 0.85. By adding this quantity to the current soil Index for copper or zinc,
we can predict life of the site for waste disposal.
In addition to copper and zinc indices,this table also provides a summary of lime recommendations for each crop
based on the first crop listed on the most recent soil sample.Application of lime at recommended rates Is
necessary to maintain soil pH in the optimum range for crop production.If the first crop or rotation changes,these
recommendations may need to be reevaluated to ensure optimal ranges ofr crop production are maintained.
Tract ID F191d ID Crop(s) pH UM* tbLcom. Cua ¢opps�� Zna ZI
foE¢rop(e) Recom�is�Sdedon Recommf atlon
Oasli i )
2339 1 6.3 0,0 55 0,0 38 0,0
2350 1 5.5 0,0 70 0.0 75 0.0
2385 1 5.7 0.0 130 0.0 135 0,0
2365 2 6.8 0.0 145 0,0 170 0,0
2400 1 5.6 0.0 45 0.0 58 0,0
2708 5 6.4 0.0 55 0.0 70 0.0
2708 6 5.8 0,0 65 0.0 70 0.0
2708 8 5.3 0,0 65 0,0 53 0.0
2708 10 6.4 0.0 55 0.0 70 0,0
2757 1 5.6 0,0 55 0.0 95 0,0
9538 1 5.7 0.0 55 0.0 93 0,0
9566 1 6.1 0,0 55 0.0 93 0,0
10283 1 6.1 0.0 100 0,0 95 0.0
12032 1 80 0,0 100 0.0 105 0,0
12614 1 5.2 0.0 60 0.0 75 0.0
12830 1 5.7 0,0 55 0.0 80 0.0
12831 1 6.3 ,0 125 0,0 90 0.0
8/7120231:01:05 PM 1 12

Required Soil Test Values
J-Caine Inc
Zinc and Copper Toxicity Levels In Soils
Metal Soil Test Index Recommended Action
Zn 300 Limit application on peanuts.Maintain soil pH—6.0.
500 Cease application on peanut land.Maintain soil pH>=6.0.
2000 Caution:seek alternative site(all crops).Maintain soil pH>=6.0.
3000 Cease application(all crops).Maintain soil pH>=6.0.
Cu 2000 Caution:seek alternative site(all crops).Maintain soil pH—6.0.
3000 Cease application(all crops).Maintain soil pH—6.0.
6/7/20231:01:05 PM 2/2

Planned Crops Summary
J-Caine Inc
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 I Field I Tetrad I WetfaWe BMU Lf Crop Narbe RYE fin- PLAT C 4(Itaa/acre)
Acres Aar'as d"" rop
P fler4wi Apphed
2339-r 1 I 51.5 51.6 Bab 16
Wheat,Grain 74 Bushels 84 Medium 37 NA
2350 r 1 113.04 113.04 BaB 1b
Wheat,Grain 95 Bushels 101 Medium 48 NA
2365 1 33.09 33.09 BaB 15
Wheat,Grain 95 Bushels 101 1 Medium 48 NA
2385 1 2 10.82 10.82 BaB 46
Wheat,Grain 100 Bushels 178 Medium 50 NA
2400— 1 50 50 Mh8 10
Fescue Pasture 3 Tons 110 Medium 5 NA
2708— 5F 8.98 8.98 8813 8
Wheat,Grain 74 Bushels 132 Medium 37 NA
2708— 6 �.44 5.44 BaB 10
Wheat,Grain 95 Bushels 11691 Medium 48 NA
2708— 8 5.31 5.31 Bab 10
Wheat,Grain 95 Bushels 101 Medium 48 NA.
2708— 10 2.03 2.03 BaB 15
Wheat,Grain 95 Bushels 101 1 Medium 48 NA.
2757— 1 22.57 22.67 Be¢ 10
Wheat,Grain 74 Bushels 132 Medium 371 NA
9538— 1 48.28 46.28 Bab 15
Wheat,Grain 95 Bushels 101 Medium 48 NA
9566— 1 F28.5 28.5 18D 10
Wheat,Grain 74 Bushels 132 Medium 37 NA
8/7/2023 12:59:09 PM 1/2

Planned Crops Summary
J-Caine Inc
10283- 1 12.84 14.84 800 15
Wheat,Grain 80 Bushels 142 Medium 40 NA'
12032- 1 12.36 12.38 Kk6 10 _
Wheat,Grain 93 Bushels __`_166 Medium_ 46 NA
12614- 1 161.94 161.94 Bab 15
Wheat,Grain 95 Bushels 169 Medium 48 NA
12830- 1 9.32 9.32 Be6 15
Wheat,Grain 95 Bushels 169 Medium 1 48 NA'
12831- 1 1 22.9 22.9 TbB 15
Wheat,Grain 1 95 Bushels 1 169 Low 48 NA
Totals: 596.92 596.92
Notes:1.In the tract column,-symbol means leased,otherwise,owned.
L/ Poteriddl Leaching Technical Guidance
Low potential to contribute to soluble nutrient None
<2 leaching below the root zone.
Moderate potential to contribute to soluble nutrient Nutrient Management(590)should be planned. !
i
>=2&<=10 leaching below the root zone.
High potential to contribute to soluble nutrient Nutrient Management(590)should be planned.Other conservation
i leaching below the root zone. practices that improve available water holding capacity of soil 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
Stdps(393)and Riparian Forest Buffers(391).
PL Loss Index Rating P Management Recommendagon
r 0-25 Low No adjustment needed;N based application
r 26-50 Medium No adjustment needed; N based application
51 - 100 High Application limited to crop P removal
> 100 Very High Starter P application only
817/202312:59:09 PM 2/2

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

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

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

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
be maintained for five (5) years.
23. Dead animals will be disposed of in a manner that meets North Carolina
regulations.

u21—M 0 N RCS
Nnitod uralF ourcin eConseeMonSmIchun NUTRIENT MANAGEMENT PLAN
Natural Resources Conservatan Service
SUPPLEMENTAL INFORMATION
N.C. Practice Job Sheet: NC-590
Prepared for: -S-ct4226 A,3c
By: Qn- SIC
Farm: Tract(s): Dater
WHAT IS NUTRIENT MANAGEMENT?
Nutrient Management is applying nutrients
from all sources with the right placement, in fertilizer and manure application methods.
the right amount, at the right time, and from When precision ag/variable rate application
the right source to minimize nutrient losses to technology is utilized, see the next section of
surface and groundwater. This practice is this Job Sheet for additional guidance on plan
accomplished through development and requirements.
implementation of a Nutrient Management
Plan,which can be part of a broader • aerial site photograph(s)/imagery or site
Conservation Plan or CNMP that addresses map(s),and a soil survey map of the site,
multiple resource concerns. . Sufficient soils information—such as dominant
PURPOSE OF NUTRIENT MANAGEMENT soil map until for each planned field—needed
to apply nutrients at RYE and Soil Test Report
determined rates as appropriate;and to not
A nutrient management plan is intended to exceed rates determined by nutrient risk
accomplish one or more of the following assessment planning criteria.
objectives: . location of designated sensitive areas and the
associated nutrient application restrictions and
• To budget, supply, and conserve nutrients for setbacks,
plant production. . results of approved risk assessment tools for
• To minimize agricultural nonpoint source any necessary evaluations for nitrogen,
pollution of surface and groundwater phosphorus,and erosion losses.
resources. . current and/or planned plant production
• To properly utilize manure or organic by- sequence or rotation,
products as a plant nutrient source. . soil,water,compost, manure,organic by-
• To protect air quality by reducing odors, product,and plant tissue sample analyses
nitrogen emissions(ammonia,oxides of applicable to the plan. Where non-NCDA soil
nitrogen),and the formation of atmospheric testing labs are used, nutrient
particulates. recommendations must be made using NCDA-
• To maintain or improve the physical,chemical, similar guidelines and methodologies. Note:
and biological condition of soil. high levels of soil copper and zinc may be toxic
to production crops. Land application of these
nutrients must be accordance with
CONTENTS OF THE NUTRIENT NCSU/NCDA crop toxicity guidelines.
MANAGEMENT PLAN Realistic yield goals for the crops planned for
The following components are included in nutrient application,
nutrient management plan specifications
typical of more'traditional'
NC-590 lob Sheet May 2015 page 1

• Planned nitrogen application rates based on rates must be provided as specifications prior
NC Realistic Yield Expectations(RYEs)or to application.
sufficiently documented yield records,
• Ngjg—where Diammonium phosphate(18-46-
• The Nitrogen Leaching Index for planned 0)is the primary variable rate P fertilizer
fields, source applied on legume crops,additional N
• Planned P&K application rates based on soil will likely be needed to achieve RYEs.
test results(see next section where P&K The plan was developed based on the current
applied through variable rate technology). NRCS 590 standard and Federal,state, or
• listing and quantification of all nutrient sources local regulations or policies. Changes in laws
and form,including starter fertilizer or regulations may require a plan modification.
applications and legume-based cover crop This Job Sheet is a required supplement to
mixes. the Nutrient Management Plan.
• in accordance with the nitrogen and NC Permitted Animal Operations: For NC
phosphorus risk assessment tool(s),specify
the recommended nutrient application source, DENR-DWR or NPDES permitted animal
timing,amount(except for precision/variable operations,the waste utilization portion of the
rate applications specify method used to Certified Animal Waste Management Plan
determine rate),and placement of plant (CAWMP)must meet requirements specified by
nutrients for each field or management unit, the Permit. The NC 1217 Interagency Group
and provides guidance on the required minimum
elements of a CAWMP. This guidance is found in
• guidance for implementation,operation and Sec 1.1 of the latest 1217 Guidance Document,
maintenance,and recordkeeping as specified located at:
by the CNMP or applicable NC DWQ or http://www.nca4r.gov/SWC/tech/guidancedocumen
NDPES permit. ts.html.
Where precision/variable rate nutrient
application applications are planned and Nitrocien Leachina Index Values
made, some required planning components of Nitrogen Leachino Index values,obtained throuah
the preceding section may be provided by the use of current Soil Hydrologic Group(SHG)-based
overall conservation plan. In addition,the LI index maps in Sec II of the NC FOTG or RUSLE
following components required in nutrient 2 field-specific soil loss calculations,are included
9 p are q in the Nutrient Management Plan. SHGs per soil
management planning. map unit are available through selection of the Soil
Data Explorer and Soil Properties and Qualities
• The goo-referenced field boundary and data (then select"Soil Qualities and Features")tabs
collected that was processed and analyzed as once an Area of Interest has been defined in
a GIS layer or layers to generate nutrient or NRCS Web Soil Survey.
soil amendment recommendations.
• Planned nitrogen application rates based on If the Nitrogen Leaching Index> 10 for planned
fields,appropriate conservation practices must be
NC RYEs or sufficiently documented yield included in a conservation plan to prevent nitrogen
records from leaving the field via surface or subsurface
• The Nitrogen Leaching Index for planned runoff.
fields. Below are conservation crop management
• The nutrient recommendation guidance and techniques and practices recommended for
recommendation equations used to convert the mitigation of nitrate losses(practices also
GIS base data layer or layers to a nutrient documented in conservation plan):
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 Sheet May 2015 page 2

NUTRIENT MANAGEMENT PLAN PLAT Categorical Ratings Information
DEVELOPMENT When soil test phosphorus continues to increase
The nutrient management plan has been on a long term basis, PLAT may produce results
developed to meet nutrient application rate criteria that require P-based manure application planning
for all sources of nitrogen, phosphorus, potassium and planning for no additional manure P.
as specified by NRCS 590 Nutrient Management Conditions that will require P-based or no-P
standard criteria. planning will be based on site specific resource
conditions,which will facilitate data input into
In addition to NCDA Agronomic Division soil test PLAT. PLAT categorical ratings that will require
recommendations,or soil test recommendations enhanced P application planning are:
made through similar guidelines,the plan is based
on NC INMC approved values for realistic yield HIGH: P-based manure application is required
goals,nitrogen factors, phosphorus removal rates, (limited to P uptake in harvested crop biomass)
default nutrient values for animal waste,plant
availability coefficients for N,P,and K,and animal VERY HIGH: No additional manure P or starter P
waste generation volumes where applicable. application to be specified in nutrient management
Approved values are found at: plan.
htto://nutrients.soil,ncsu,edurndex.htm
Where manure is applied,farm records may also Phosphorus Drawdown Strategy
be used through a procedure provided in SIB 1217 Information:
Interagency Group guidance,available at: Implementation of a phosphorus'drawdown'
htto://www.ncacr.aovlSWCltech11217committee.ht strategy may be a consequence of PLAT results,
m/ or may be requested in order to lower soil test
phosphorus levels.
For NC permitted animal operations,planning Should a reduction in soil test P be desired or
requirements for Plan"Amendments"(minor necessary,the only currently proven method of
modifications)and"Revisions"(Major substantial P'drawdown'is to not apply manure-
Modifications)are clarified by SB 1217 Interagency based P and to plant and harvest crops that utilize
Group Guidance. P currently-present in the soil surface.
Crop specific estimated annual P removal amounts
ADDITIONAL PHOSPHORUS-RELATED are available on the NCSU Nutrient Management
PLAN INFORMATION (Applicable when in NC website:
increases in Soil Test P are expected on httr)://nutrients.soil.ncsu.edu/vields/index.php
the planned area) Conservation Practices and Management
In NC,a field-specific Phosphorus Loss Techniques to Reduce P Loss Potential:
Assessment Tool(PLAT)evaluation is completed Conservation practices,especially those that
in accordance with 590 Nutrient Management prevent soil particle detachment and trap sediment
standard General Criteria requirements,and at field edges are effective in preventing
phosphorus must be applied in accordance with phosphorus movement from the planned site.
590 standard Manure Phosphorus Application Manure application techniques can also be applied
Rates. to reduce P loss risk. These practices must be
In addition to the basic plan components,plan included in the conservation plan where
information on PLAT categorical ratings, P determined PLAT risk=HIGH for planned fields.
drawdown strategies,and conservation practices Consult the conservation plan developed in
to reduce P loss risk is required when increases in conjunction with the nutrient management plan for
Soil Test P are expected on the planned area. information on practices recommended to reduce
Typically,this could occur when manure is phosphorus AND nitrogen loss risks. Application
consistently applied at Nitrogen-based rates. High management techniques to reduce nutrient loss
levels of phosphorus in the surface soil layer have risk may be prescribed below:
been linked to increasing risk of P loss through
surface runoff and leaching.
0 Increases in Soil Test P are expected
on the planned area(not typical ii P
application made per soil test results).
NC-590 Job Sheet May 2015 page 3

Long Term Strateav for Reduction of Soil P RECORDKEEPING
Levels: Waste reports from the NCDA&CS Agronomic
As noted in the P drawdown strategy section,the Division,or equivalent,are acceptable sources of
only currently proven method for reducing high information for determining applied manure nutrient
levels of soil P is not applying P, paired with amounts for recordkeeping or crop budgeting
producing crops on the planned site that use purposes.
existing soil P. Where soil P and PLAT
evaluations indicate an increasing risk to water Records must be maintained for at least 5 years,or
quality,substantially reducing soil P levels through for time and manner required by Permit for animal
crop uptake can take many years of operations to document plan implementation and
implementation. When P is not applied,and maintenance.As applicable,records include:
existing soil P is used by crops,eventually,soil will • soil,plant tissue,water, manure,and
become P deficient. Consult CES or NCDA organic by-product analyses resulting in
Regional Agronomy specialists for additional recommendations for nutrient application,
information soil test P reduction timelines. . quantities,analyses and sources of
Manure P produced in excess of crop nutrients applied,
requirements: • dates,and method(s)of nutrient
Consult the nutrient management plan for a applications,source of nutrients,and rates
quantification of manure generated by the animal of application,
feeding operation that may exceed crop P . weather conditions and soil moisture at the
requirements. time of application; lapsed time to manure
incorporation; rainfall or irrigation event,
"Manure Hauler" Information . crops planted,planting and harvest dates,
All manure waste applied on land owned by or yields,nutrient analyses of harvested
controlled by the Animal Feeding Operation(AFO) biomass,and crop residues removed,
owner or operator must be included in the nutrient . dates of plan review,name of reviewer,
management plan.The volume difference in total and recommended changes resulting from
manure waste generated by the AFO and waste the review,and
applied to land not owned or controlled by the . all enhanced efficiency fertilizer products
producer must be accounted for in a nutrient y
management plan. used.
General information on manure waste generated Additional records for precision/variable rate
by an AFO to be applied to land not owned or sites must include:
controlled by the AFO owner or operator may be . maps identifying the variable application
recorded as specified in the NC CNMP source,timing,amount,and placement of
Certification Sheet and Documentation Checklist or all plant nutrients applied,and
other supplemental documentation to the nutrient
management plan. NRCS CNMP technical criteria • GPS-based yield maps for crops where
require documentation of manure exports off the yields can be digitally collected.
farm (this can be done below). The AFO . Documentation per field nitrogen
owner/operator should provide the third party application rates do not exceed RYE-
applicator with a current waste analysis in order to based recommended rates
facilitate agronomic crop application of the facility's
generated waste. Should land not owned or • Documentation that applied phosphorus
controlled by the AFO owner or operator be and potassium recommendations do not
included in a nutrient management plan,the exceed recommended rates specified by
complete plan must meet 590 criteria. soil tests.
Type and Quantity of Animal Feeding Operation . For non-variable rate application of P&K.
(AFO)manure generated by the facility: provide applied map with field boundaries
indicating source,timing,method,and rate
of all applications.
Quantity of AFO manure generated to be exported . Where'chlorophyll reader technology is
off the farm for third party application: utilized,application records that nitrogen
rates match RYE-based N rates as closely
as possible.
NC-590 Job Sheet 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

Poultry Farm Waste Management Odor Control Checklist
Source Cause BMPs to Minimize Odor Site Specific Practices
Farmstead • Poultry production O Vegetative or wooded buffers
O Recommended best management practices
O Good judgment and common sense
Floor surfaces . Wet dirty surfaces O Scrape manure,dust,feathers into collection
(walk aisles) alleys
O Splash boards along upper ends of collection
alleys
O Proper ventilation
Cage manure . Manure-covered surfaces O Scrape manure into collection alleys
dropping boards
Manure collection . Partial microbial O Frequent manure removal by Flush or scrape
alleys decomposition O Frequent checks and maintenance on waterers
and water pipes
Ventilation exhaust . Volatile gases O Fan maintenance
fans . Dust O Efficient air movement
Indoor surfaces . Dust O Vacuum or washdown between Flocks
Manure conveyors • Partial microbial O Keep mechanical equipment in good repair
decomposition O Remove manure accumulations promptly
Storage tank or • Partial microbial O Bottom or midlevel loading
basin surface decomposition O Tank covers
• Mixing while filling O Basin surface mats of solids
Agitation when emptying O Proven biological additives or oxidants
•
Manure slurry or • Agitation when spreading O Soil injection of slurry sludges
sludge spreader • Volatile gas emissions O Wash residual manure from spreader after use
outlets O Proven biological additives or oxidants
AMOC-November 1 I, 1996,page I

Poultry Farm Waste Management Odor Control Checkllst
Source Cause BMPs to Minimize Odor Site Specific Practices
Dead birds • Carcass decomposition O Proper disposition of carcasses
Dead bird disposal • Carcass decomposition O Complete covering of carcasses in burial pits
pits O Proper location/construction of disposal pits
O Disposal pit covers tight fitting
Standing water • Improper drainage O Grade and landscape such that water drains away
around facilities • Microbial decomposition of from facilities
organic matter
Mud tracked onto . Poorly maintained access O Farm access road maintenance
public roads from roads
farm access
Additional Information: Available From:
Poultry Manure Management;.0200 Rule/BMP Packet NCSU,County Extension Center
Poultry Layer Production Facility Manure Management:High Rise,Deep Pit;EBAE 131-88 NCSU BAE
Poultry Layer Production Facility Manure Management:Undercage Flush Lagoon Treatment; EBAE 130-88 NCSU BAE
Lagoon Design and Management for Livestock Manure Treatment and Storage;EBAE 103-83 NCSU BAE
Calibration of Manure and Wastewater Application Equipment;EBAE Fact Sheet NCSU BAE
Proper Disposal of Dead Poultry;PUT Guide No. 19 NCSU Poultry Science
Nuisance Concerns in Animal Manure Management:Odors and Flies;PRO107, 1995 Conference Proceedings Florida Cooperative Extension
AMOC-November 11, 1996,page 3

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 for the fields where runoff occurred.
C: Leakage from the waste pipes and sprinklers-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.
1 December 18, 1996

4: If none of the above works call 911 or the Sheriffs Department and explain your problem to
them and ask that person to contact the proper agencies for you.
5: Contact the contractor of your choice to begin repair of problem to minimize off-site damage.
a. Contractors Name:
b. Contractors Address:
c. Contractors Phone:
6: Contact the technical specialist who certified the lagoon(MRCS, Consulting Engineer, etc.)
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 from happening again.
3 December 18, 1996

T
SHWT Elevation
2
SHWT Elevation = 33.88 ft.
3
SHWT Elevation = 33.29
Bottom of Lagoon - r,
4 Elevation = 38.0 ft. s;' ,I , IIf �' `; r
SHWT Elevation = 33.88 ft. ?Jy f C
5
A
SHWT Elevation = 35.35 ft. / K=
tr Y.
6 � h i b R rAi
zr >
SHWT Elevation = 35.29 ft.
8
SHWT Elevation = 34.10 ft.
SHWT Elevation = 35.84 ft.
i I
-n i t i• l i I
•0 300 Feet _
72
Amick Lagoon Closure Date: November 1, 2023
Location: Near 760 Sides Rd., Albemarle,
Legend SOIL INVESTIGATION - ELEVATION OF SHWT NC (GPS Coordinates: 35.281, -80.2468)
0 Soil Borings STANLY COUNTY, NC Map Created by: Patrick Mitchell, LSS
Surface Waters �0Au.ruk
T
Parcels NORTH CAROLINA DIVISION OF
SOIL & WATER
A
1312
' fl
• �DNDEDI - NORTH

QDANRCS VA RUSLE2 Plan Printout Summary
Summary of RUSLE2 calculation for multiple fields, one or more management alternatives per field
Client/Owner name: J Caine
Tract#:
Location: USA\North Carolina\Stanly County
Printout date: July 17, 2023
Prepared b (name):
USDA Service Center/Location:
Narrative description of plan, fields, and/or management alternatives being compared:
Info: Closure plan
Notes on collection of input data, field visits, etc.:
Summary of RUSLE2 output for each field & management alternative:
Field Field(if Cons.plan. soil loss, Soil conditioning index STIR
name applicable) t/acl r (SCI) value
T 12830 1,2,4 0.52 0.66 3.0
T12830 5, 6 0.41 0.67 3.0
T9566 0.52 0.66 3.0
T8532 12 0.41 0.67 3.0
T12831 11 0.48 0.67 3.0
T12831 14 0.42 0.67 3.0
T2708 5, 11 0.52 0.66 3.0
T2708 6, 8, 10 0.41 0.67 3.0
T2339 0.52 0.66 3.0
T12614 0.41 0.67 3.0
T2350 0.41 0.67 3.0
T9538 0.41 0.67 3.0
T12032 0.45 0.67 3.0
T2400 0.23 0.98 0.90
T10283 0.41 0.67 3.0
T2757 0.52 0.66 3.0
T2365 1,2, 3,4, 11 0.41 0.67 3.0
T2365 6, 8 0.39 0.67 3.0
T2365 7 0.52 0.66 3.0
Recommendations i Comments:
VA RUSLE2 Plan Printout Summary, July 17, 2023 1

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 12830
Field ID: Field ID: 1
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .41 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 9" 39
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 1
Soluble P = 1
Leachate P = 0
Source P = 29
Total P Rating = 31 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00;00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 12614
Field ID: Field ID: 1
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P205: 10.63 lbs
Application Method: Broadcast
Soil Loss: .41 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 67
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 2
Leachate P = 0
Source P = 29
Total P Rating = 33 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 12032
Field ID: Field ID: 1
Soil Series: KkB: Kirksey silt loam, 0 to 6 percent slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .45 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 6.7
WV_Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 0
Soluble P = 0
Leachate P = 0
Source P = 29
Total P Rating = 29 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 10283
Field ID: Field ID: 1
Soil Series: BaD: Badin channery silt loam, 8 to 15 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .41 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0'• - 4" 67
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 2
Leachate P = 0
Source P = 29
Total P Rating = 33 (Medium)

PLAT Results For: Stanly 7/18/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2350
Field ID: Field ID: 1
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P205: 10.63 lbs
Application Method: Broadcast
Soil Loss: .41 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0^ - 4" 61
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 2
Leachate P = 0
Source P = 29
Total P Rating = 33 (Medium)

PLAT Results For: Stanly 7/18/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2365
Field ID: Field ID: 1
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .41 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 41' 92
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 3
Soluble P = 3
Leachate P = 0
Source P = 29
Total P Rating = 35 (Medium)

PLAT Results For: Stanly 7/18/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2400
Field ID: Field ID: 1
Soil Series: MhB: Misenheimer channery silt loam, 0 to 4
percent slopes
Crop: Fescue Pasture
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40. 62 1000 gal
Lb P205: 10. 63 lbs
Application Method: Broadcast
Soil Loss: .23 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 33
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 0
Soluble P = 3
Leachate P = 0
Source P = 34
Total P Rating = 37 (Medium)

PLAT Results For: Stanly 7/18/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2708
Field ID: Field ID: 6
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40. 62 1000 gal
Lb P2O5: 10. 63 lbs
Application Method: Broadcast
Soil Loss: .41 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 77
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 3
Leachate P = 0
Source P = 29
Total P Rating = 34 (Medium)

PLAT Results For: Stanly 7/18/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2708
Field ID: Field ID: 10
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .41 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 62
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 2
Leachate P = 0
Source P = 29
Total P Rating = 33 (Medium)

PLAT Results For: Stanly 7/18/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 9538
Field ID: Field ID: 1
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40. 62 1000 gal
Lb P2O5: 10. 63 lbs
Application Method: Broadcast
Soil Loss: .41 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 74
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 3
Leachate P = 0
Source P = 29
Total P Rating = 34 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 12831
Field ID: Field ID: 1
Soil Series: TbB: Tarrus channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .42 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 82
WV Factor (USER) 0
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 3
Soluble P = 1
Leachate P = 0
Source P = 15
Total P Rating = 19 (Low)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2757
Field ID: Field ID: 1
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .52 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 9" 53
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 2
Leachate P = 0
Source P = 29
Total P Rating = 33 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2708
Field ID: Field ID: 8
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .52 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 42
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 1
Leachate P = 0
Source P = 29
Total P Rating = 32 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2708
Field ID: Field ID: 5
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40. 62 1000 gal
Lb P205; 10. 63 lbs
Application Method: Broadcast
Soil Loss: .52 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 411 62
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 2
Leachate P = 0
Source P = 29
Total P Rating = 33 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2365
Field ID: Field ID: 2
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40. 62 1000 gal
Lb P2O5: 10. 63 lbs
Application Method: Broadcast
Soil Loss: .39 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 176
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 5
Soluble P = 6
Leachate P = 0
Source P = 29
Total P Rating = 40 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 2339
Field ID: Field ID: 1
Soil Series: BaB: Badin channery silt loam, 2 to 8 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .52 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 57
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 2
Leachate P = 0
Source P = 29
Total P Rating = 33 (Medium)

PLAT Results For: Stanly 8/7/2023 12:00:00 AM
INPUTS
County: Stanly
Tract ID: Tract ID: 9566
Field ID: Field ID: 1
Soil Series: BaD: Badin channery silt loam, 8 to 15 percent
slopes
Crop: Wheat, Grain : Conservation Tillage - high
residue
Fertilizers: Liquid for Mixing
Yearly Applied Amount: 40.62 1000 gal
Lb P2O5: 10.63 lbs
Application Method: Broadcast
Soil Loss: .52 t/ac/yr
Receiving Slope Distance 0-9 ft
Soil Test 0" - 4" 53
WV Factor (USER) 0
Artificial Drainage System: NO
Hydrologic Condition: GOOD
OUTPUTS
Particulate P = 2
Soluble P = 2
Leachate P = 0
Source P = 29
Total P Rating = 33 (Medium)

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