350056_Waste Utilization Plan_Closure_SDAP_20240212

Peachtree Creek SDAP
This plan has been prepared for:
Peachtree Creek
Lamont Futtrell
4923-C Bloomery Rd
Wilson, NC 27896
252-235-8642
5/26/2023
This plan has been developed by:
Franklin County Soil and Water
Conservation District
Quinton Cooper
101- B S. Bickett Blvd.
Louisburg, NC 7549
919-4
D eloper S &
Type of Plan: Nutrient Management with Closure Cleanout 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.
37
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:
3r 23
T nical Spec list nature Date

Sources in Plan
Peachtree Creek SDAP
Nutrients applied in accordance with this plan will be supplied from the
following source(s):
Commercial Fertilizer is included in this plan.
U 1008
Peachtree Lagoon 3 Closure Source waste generated 2,367,066 gals/year by a 0 Swine Lagoon
Sludge - Farrow -Finish operation. This production facility has waste storage capacities of
approximately 0 days.
Estimated Pounds of Plant Available Nitrogen Generated per Year
Injected
17,128
Incorporated-4 wks or less following
application
17,128
Incorporated-5 wks to 3 mos
following application
14,273
Broadcast
14,273
Irrigated
14,273
Max. Available
PAN (Ibs) "
Actual PAN
Applied (Ibs)
PAN Surplus /
Deficit (Ibs)
Actual Volume
Applied (Gallons)
Volume Surplus/ Deficit
(Gallons)
Year 1
14,273
15,487
(1,214)
2,568,356
(201,290)
2/9/2024 9:23:21 AM 1 / 1

Waste Storage Closure Source Description
Peachtree Creek SDAP
SOURCE: Peachtree Lagoon 3 Closure Source
Date Measured: 11/01/2022
Lagoon Dimensions: TOP - 580 X 273; BOTTOM - 575 X 268; SIDE SLOPES - 2.5:1
Liquid Depth: 4.10 ft.; Liquid Volume: 4,319,970 gallons.
Sludge Depth: 3.80 ft.; Sludge Volume: 3,559,604 gallons
Liquid Depth: 4.50 ft.; Liquid Volume: 2,336,757 gallons.
Sludge Depth: 3.21 ft.; Sludge Volume: 1,431,132 gallons
Liquid Depth: 2.95 ft.; Liquid Volume: 1,400,177 gallons.
Sludge Depth: 2.90 ft.; Sludge Volume: 966,889 gallons
Waste Sample #: FY23-
W 002391
Waste Sample #: FY23-
W002375
Waste Sample #: LAG2LQ
Waste Sample #: FY23-
W002374
Waste Sample #: FY23-
W 002391
Waste Sample #: FY23-
W002374
U 1008
Peachtree Lagoon 3 Closure Source 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 2,367,066 gals in this structure prior to closure.
Estimated Plant Available Nitrogen
Application Method
(Ibs N/1000 gals)
Source Total (Ibs)
Injected
7.24
17,128
Incorporated-4 wks or less following
application
7.24
17,128
Incorporated-5 wks to 3 mos following
application
6.04
14,273
Broadcast
6.04
14,273
Irrigated
6.04
14,273
Max. Available PAN (Ibs) '
Actual PAN Applied (Ibs)
PAN Surplus / Deficit (Ibs)
Actual Volume Applied
(Gallons)
Volume Surplus/ Deficit
(Gallons)
14,273
15,487
(1,214)
2,568,356
(201,290)
Note: In Source ID, S means standard source, U means user defined source.
Maximum PAN Available is calculated on tjhe basis of the actual application method(s) identified in the plan for this source.
2/9/2024 9:23:07 AM 1 / 1

Planned Crops Summary
Peachtree Creek SDAP
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 Wettable I SMU I LI Crop Name RYE Recom- I PLAT P205 (lb s/acre)
Acres Acres mended Rating Crop
PAN Removal Applied
1..__„ 53;41 53.41 12°Soybeans, Manured, Full Season uW W W W Wr 39 BushelsW 1521 Medium
605 —
2
26
26
WeCl
12
Soybeans Manured Full Season
37 Bushels
144 Medum
605
9
37.1
37.1 W eC
12
.......... ...
_. . -
Soybeans, Manured, Full Season
_ _
37 Bushels
_
152
_ ,_
Medium
Totals:
1
116.50
116.50
Notes: 1. In the tract column, — symbol means leased, otherwise, owned.
31
High potential to contribute to soluble nutrient Nutrient Management (590) should be planned. Other conservation
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
Strips(393) and Riparian Forest Buffers (391).
2/9/2024 9:26:08 AM 1 / 2

Planned Crops Summary
Peachtree Creek SDAP
P Loss Index
Rating
P Management Recommendation
0 - 25
Low
d................ ......
No adjustment needed; N based application
26..._.50 ...........................
Medium
No...ad'ustment needed; N...based application
J � pp
51 - 100
High
Application limited to crop P removal
��.... > 100��'.,�,�.�,Very
High
,.Starter P application only .... � ....
2/W2Q24 9:26:08 AM 2 / 2

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Peachtree Creek SDAP
5/26/2023
Type of Plan: Nutrient Management with Closure Cleanout Only
Narrative:
Producer is applying lagoon waste through a agitate and haul method. Producer will be closing
Lagoon 1 with EQIP and lagoon 3 with Swine/Dairy program. The addititonal 2ft +/- sludge on the
bottom of both lagoon 1 and lagoon 3 will be scraped to clay layer and applied according to the
plan that was wrote for that specific lagoon. The pipe that carries overflow from Lagoon 2 to
Lagoon 3 will be capped and no other water will not be allowed to drain into Lagoon 3. Lagoon 2
will have a new start/stop marker installed by NRCS engineer following the closure of Lagoon 1.
Lagoon 2 will need to be maintained to keep water levels within required water levels. Lagoon 3
will be converted with a engineer approved design to an agricuture use pond. All disturbed areas
will be seeded and hayed with permenant grass.
* The current fields on the map are in trees but the fields have been cleared and a mulitspecies
cover crop has been planted. The fields will be planted in full season soybeans following the
application of lagoon 3 material.
2/9/2024 9:26:24 AM 1 / 1

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Required Soil Test Values
Peachtree Creek SDAP
The Required Soil Test Values shown in the following table provide a summary of recommended actions that
should be taken based off information provided at time of soil tests. Fields that receive manure must have a soil
analysis conducted at least once every three years. High levels of zinc and copper can adversely affect plant
growth. Alternative crop sites must be used when the concentration of these metals approach excessive levels.
Site life can be estimated by dividing the amount of copper and zinc to be applied in Ibs/acre by 0.036 and 0.071,
respectively and multiplying the result by 0.85. By adding this quantity to the current soil index for copper or zinc,
we can predict life of the site for waste disposal.
In addition to copper and zinc indices, this table also provides a summary of lime recommendations for each
crop based on the first crop listed on the most recent soil sample. Application of lime at recommended rates is
necessary to maintain soil pH in the optimum range for crop production. If the first crop or rotation changes,
these recommendations may need to be reevaluated to ensure optimal ranges ofr crop production are
maintained.
Tract ID
Field ID
Crop(s)
pH
Lime Recom.
for Crop(s)
(tons/acre)
Cu-1
Copper
Recommendation
Zn-I
Zinc
Recommendation
605
1
5.4
0,0
31
0,0
60
0,0
605
2
5.4
0,0
31
0.0
60
0.0
605
9
5.9
1 0,0
84F
0,0
376
0,0
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.
2/9/2024 9:26:36 AM 1 / 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, storical data,
climatic conditions, and level of management, unless there are regulations
that restrict the rate of applications for other nutrients.
4. Animal waste shall be applied to land eroding less than 5 tons per acre per
year. Waste may be applied to land eroding at more than 5 tons per acre per
year but less than 10 tons per acre per year provided grass filter strips are
installed where runoff leaves the field (see USDA, NRCS Field Office Technical
Guide Standard 393 - Filter Strips).
s. Odors can be reduced by injecting the waste or by disking after waste
application. Waste should not be applied when there is danger of drift from
the land application field.

6. When animal waste is to be applied on acres subject to flooding, waste will
be soil incorporated on conventionally tilled cropland. When waste is applied
to conservation tilled crops or grassland, the waste may be broadcast
provided the application does not occur during a season prone to flooding
(see "Weather and Climate in North Carolina" for guidance).
7. Liquid waste shall be applied at rates not to exceed the soil infiltration rate
such that runoff does not occur offsite or to surface waters and in a method
which does not cause drift from the site during application. No ponding
should occur in order to control odor and flies.
s. Animal waste shall not be applied to saturated soils, during rainfall events, or
when the soil surface is frozen.
9. Animal waste shall be applied on actively growing crops in such a manner
that the crop is not covered with waste to a depth that would inhibit growth.
The potential for salt damage from animal waste should also be considered.
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.
i1. 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.
17. A protective cover of appropriate vegetation will be established on all
disturbed areas (lagoon embankments, berms, pipe runs, etc.). Areas shall
be fenced, as necessary, to protect the vegetation. Vegetation such as trees,
shrubs, and other woody species, etc., are limited to areas where considered
appropriate. Lagoon areas should be kept mowed and accessible. Berms
and structures should be inspected regularly for evidence of erosion,
leakage, or discharge.
18. If animal production at the facility is to be suspended or terminated, the
owner is responsible for obtaining and implementing a "closure plan" which
will eliminate the possibility of an illegal discharge, pollution, and erosion.
19. Waste handling structures, piping, pumps, reels, etc., should be inspected on
a regular basis to prevent breakdowns, leaks, and spills. A regular
maintenance checklist should be kept on site.

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