HomeMy WebLinkAbout310404_Waste Utilization Plan_20240807Mike Kennedy Farm Closure
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This plan has been prepared for: I This plan has been developed by.,
Mike Kennedy Faun NCOWS DSWC
Mike Kennedy Michael Shepherd
345 Kennedy Lane 791 S. Main St
Pink Hill NC 28572 Mocksville, NC 27028
336-940-8901
7,kce� 5
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 plant for
the faun named above. i have read and understand the Required Specifications concerning animal
waste management that are included with this plan.
�ignature (owner)
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 Sail and Water
Conservation Commission,
Plant Approved By:
Tecnnicat Specialist Signature Data
Waste Facility Closure Plan
Mike Kennedy Farm, AWS310404
345 Kennedy Ln, Pink Hill, NC 28572
This plan is for the closure of the swine lagoon structure located at Mike Kennedy's farm,
AWS310404, in Duplin County, NC. The planned closure of the structure will implement new
technologies to handle both the sludge and liquid swine waste other than the typical land
application of the waste. The closure of the lagoon will comply with Federal, State and Local laws
and rules.
Introduction
The Mike Kennedy Farm is located off Kennedy Lane, approximately 0.6 mile west of NC HWY 241
(Appendix 1 -Mike Kennedy Vicinity Map). The waste storage lagoon was certified in 1996 by Murphy
Family Farms Engineering and has an approximate surface area of 61,593 square feet. The total
estimated waste volume in the lagoon is 1,400,101 gallons of liquid and 1,124,676 gallons of sludge
for a total volume of 2,524,777 gallons (Appendix 2, Mike Kennedy Estimated Waste Volumes,
Duplin Soil and Water Conservation District).
Swine and Dairy Assistance Program (SDAP)
Mike Kennedy Farm contacted the Duplin Soil and Water Conservation District (SWCD) and the NC
Department of Agriculture to participate in the Swine and Dairy Assistance Program (SDAP) to close
the waste structure. The SDAP requires all closure to be completed according to NRCS
Conservation Practice Standard 360, Waste Facility Closure.
Erosion and Sediment Control
All disturbed areas will be re -vegetated to restore the aesthetic value and prohibit erosion of the
site. Duplin Soil and Water Conservation District will recommend vegetative materials in
accordance with NRCS Practice Standard Code 342, Critical Area Planting once final units are
determined.
Liquid and Sludge Waste Removal
The liquid and sludge in the lagoon will be removed using alternative closure methodologies to
separate the liquid and solids and allow the solids to undergo further processing and distribution.
To start, the total contents of the lagoon will be agitated to create a slurry. The slurry will then be
pumped to a Sky Pump Truck. From there the slurry will be pumped to a drying plant set up on the
side of the lagoon where the sludge will be dewatered using shakers and presses to approximately
18% moisture. All liquids will be returned to the lagoon. Once dewatered, the sludge will be
conveyor belted to awaiting trucks and transported offsite to a state permitted facility for further
processing. Agreement with the state permitted processor, Mirimichi Green, to receive the sludge
is included in appendix 3.
Impoundment Closure
The landowner intends to convert the lagoon to a freshwater pond. The structure shall be
converted to meet the NRCS Practice Standard 378, Pond. The emergency spillway has been
surveyed and designed by the Division of Soil and Water Conservation engineer (Appendix 4, Mike
Kennedy Final Spillway Design). The design engineer shall be contacted prior to installation of the
spillway and then once the spillway is installed according to the design. The final conversion will be
documented with an As -Built survey showing dam and spillway dimensions. All disturbed areas
will be seeded/mulched per NRCS Practice Standard 342, Critical Area Planting.
All waste transfer components will be removed from the facility and replaced with compacted
earthen materials or rendered unable to convey waste. At this time, it is not known whether swine
buildings will be removed or re -purposed after closure is complete. Nevertheless, all infrastructure
from the hog barns to the lagoon will be disconnected.
NRCS 360 Alternative Method of Closure Requirements
NRCS Conservation Practice Standard 360, Waste Facility Closure sets requirements for
decommissioning of lagoons that shall be met to satisfy SDAP policy requirements. The lagoon
closure at Mike Kennedy farm will be intended to fulfill the requirements of the alternative method
of closure within the Waste Facility Closure 360 CPS. To meet these requirements, the following
thresholds shall be reached:
• Once all of the sludge has been dewatered and removed, a survey of the lagoon shall be
conducted on a 25 foot grid or closer by a representative from the Division of Soil and Water
Conservation. The results of the survey shall indicate no more than 0.2 foot of sludge and
signed by Technical Specialist with the SD or SI designation.
• Once all of the sludge has been removed, a liquid waste sample shall be taken by a
representative from the Division of Soil and Water Conservation and analysis performed by
the NCDA&CS Agronomics laboratory. Results of the analysis shall indicate no more than
40 parts per million of total Nitrogen.
All thresholds described above will conform to the standards consistent with the NRCS Practice
Standard 360, Waste Impoundment Closure. If the thresholds listed above are not met, additional
sludge shall be removed and/or the liquid waste shall be land applied.
Additional Supporting Materials Attached as part of this closure plan:
Appendix 1 -Mike Kennedy Vicinity Map
Appendix 2- Mike Kennedy Estimated Waste Volumes (Duplin Soil and Water Conservation District)
Appendix 3— NC Permitted Post Processing Facility Agreement to receive sludge from Mike Kennedy
Appendix 4— Mike Kennedy Final Spillway Design
Attachment 1 - Mike Kennedy Vicinity Map
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Mike Kennedy Farm
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Attachment 2 - Mike Kennedy Estimated
Volumes (Duplin Soil & Water Conservation)
Lagoon Survey Map
Date:9/19/2023
Customer(s): Mike Kennedy
District: DUPLIN SOIL & WATER CONSERVATION DISTRICT
Legend
ROADS
A'S
100
Dbma, w6u t ce, 1!
Field Office: KENANSVILLE SERVICE CENTER
Agency: Duplin Soil & Water
Assisted By: C. Smith
DUPLIN COUNTY
SOIL & WATER
N
0 100 20F
Feet
Mike Kennedy
Suvey Readings
Total Depth
8.70
8.90
9.00
8.60
8.60
8.60
8.60
9.10
8.8
Mike Kennedy
TOO Readings
Tan of Sludge
4.20
5.30
6.80
2.80
3.60
4.20
2.00
4.50
4.2
oev &0.5'i
rr w)10.5a S
3
E'er
Sludge Depth
4.50
3.60
2.20
5.80
5.00
4.40
6.60
4.60
4.6
a;Ke,
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LAGOON CLOSURE VOLUMES
Farm Name: Mike Kennedy
County: Duplin
Prepared by: A. Quinn
Date: 9/21 /2023
Temporary benchmark description & elevation:
6.30
Input cells shown as
Lagoon top lengt 383.00
Lagoon top elev. (ft)
55.42
top section
Top of liquid elev. (ft)
51.92
Top of sludge elev. (ft)
47.72
Lagoon bottom elev. (ft)
43.12
i------------------_-----_
�
mid section
Lagoon top width (ft)
161.00 i
Side slope (_ 1)
3 i
lagoon bottom
LAGOON LIQUID VOLUME
Dimensions at liquid surface:
_
Length = 362.00 ft
Width = 140.00 ft
Depth = 4.20 ft
Volume in Cubic Feet =
187,179 cubic feet
Add 20% for washdown
Volume in Gallons =
1,400,101 gallons
504,955.39 gallons
3,029,732 TOTAL
Top = 50680 sq ft
_
_
Mid = 44513.56 sq ft
349.40 ft
X 127.40 ft
Bottom = 38664.64 sq ft
336.80 ft
X 114.80 ft
LAGOON SLUDGE VOLUME
Dimensions at sludge surface
Length = 336.80 ft
Width = 114.80 ft
Depth = 4.60 ft
Volume in Cubic Feet =
150,358 cubic feet
Volume in Gallons =
1,124,676 gallons
Top = 38664.64 sq ft
Mid = 32623 sq ft
323.00 ft
X 101.00 ft
Bottom = 26962.24 sq ft
_
309.20 ft
X 87.20 ft
_
Total Volume in Cubic Feet =
337,637 cubic feet
Total Volume in Gallons =
2,524,777 allons
Farm Name: Mike Kennedy Landowner
County: Duplin
VOLUME TO BE REMOVED
Length (Top)
Width (Top)
Total Depth
Side Slopes
Liquid Depth (ft)
Sludge Depth (ft)
Freeboard (ft)
383.00
161.00
12.30
3
4.20
4.60
3.50
Note: Enter horizontal # for side slopes
Example: For 3:1 side slopes, enter 3
12.30 Survey Waste
Length
Width
Add 20% for washdown
Lagoon Dims. @ Liquid Level
362.00
140.00
504,955.39
Lagoon Dims. @ Sludge Level
336.80
114.80
3,029,732.33
Lagoon Dims. @ Bottom
309.20
87.20
Liquid
Sludge
N Value from Waste Sample
Ibs/1000 gallons
P Value From Waste Sample
Ibs/1000 gallons
Cubic Feet
Gallons
Liquid Depth
187,179.22
1,400,100.54
Sludge Depth
150,357.81
1,124,676.40
Total
337,537.02
2,524,776.94
Design
SURVEY
Top of Dike Elevation
109.00
Freeboard
3.50
Bottom of Lagoon Elevation
98.50
Avg Depth
8.8
Depth of Lagoon From Design
10.50
12.30
Field Data
10.52
TBM
60.52
HI
8.60
Water Level
51.92
elev @ W/L
50.00
Elevation
5.10
lowest pt on dike
55.42
elev @ Top of Dike
43.12
Bottom Elev
47.72
Top of Sludge Elev
4.60
sludge Depth
3.50
free board
Calcu laficava
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Attachment 3 - NC Permitted Post
Processing Facility Agreement to Receive
Sludge from Mike Kennedy Farm
NC.
MIRIMICHI GREEN -
Activate Nature
August 5, 2024
To Whom it may concern,
We intend to receive The sludge product from Mike Kennedy's farm in Pink Hill
Mirimichi Green, permit number WO 0039183.
Best regards,
Web Cowden - COO
Mirimichi Green Express, LLC
Mirimichi Green Express, LLC / 418 Hermitage Rd. Castle Hayne, NC 28429 / 910-602-1681 (Office) / 910-602-1685 )Fax)
w-mirimichigreen.com
Attachment 4 - Mike Kennedy Final Spillway
Design
TBD - Mike Kennedy Final Spillway Design
USDA
United States Department of Agriculture 360-CPS-1
Natural Resources Conservation Service
CONSERVATION PRACTICE STANDARD
WASTE FACILITY CLOSURE
CODE 360
(no)
DEFINITION
The decommissioning of a facility where agricultural waste has been treated or stored, and is no longer
used for the intended purpose.
PURPOSE
The practice is implemented to —
Protect the quality of surface water and groundwater resources
• Mitigate air emissions.
• Eliminate a safety hazard for humans and livestock.
• Safeguard the public health.
CONDITIONS WHERE PRACTICE APPLIES
This practice applies to an agricultural waste facility or livestock production site that is no longer needed
as a part of a waste management system and is to be permanently closed or converted for another use.
These facilities include liquid/dry waste storage or treatment facilities, confined animal housing, feedlots,
livestock yards, and animal mortality or composting facilities.
This practice applies where impoundments that are to be converted to fresh water storage meet the
current NRCS conservation practice standard to which the impoundment is proposed to be converted.
This practice applies to rehabilitation of soil contaminated by agricultural wastes that have been stored or
treated onsite.
This Practice does not apply to an agricultural waste facility that will be expanded or rehabilitated. Use
NRCS Conservation Practice Standards (CPSs) Waste Storage Facility (Code 313) or Waste Treatment
Lagoon (Code 359), respectively, for rehabilitated or expansion of an existing waste storage facility or
treatment lagoon.
This practice does not apply to the demolition of components such as confined animal housing,
feedbunks, or fencing. Use NRCS CPS Obstruction Removal (Code 500) for structures not directly
transferring or controlling manure to waste facility.
This Practice does not apply to sites contaminated by materials that require the issuance of a hazardous
waste permit, such as fuel or pesticides.
NRCS reviews and periodically updates conservation practice standards. To obtain the current NRCS, NC
version of this standard, contact your Natural Resources Conservation Service State office or October 2023
visit the Field Office Technical Guide online by going to the NRCS website at
https://www.nres.usda.gov/ and type FOTG in the search field.
USDA is an equal opportunity provider, employer, and lender.
360-CPS-2
CRITERIA
General Criteria Applicable to All Purposes
All Federal, State, and local laws, rules, and regulations, including National Pollutant Discharge
Elimination System (NPDES) requirements, shall be adhered to during the closure of a waste facility.
Waste transfer components that convey waste materials to a treatment or storage facility and facility
components that provide drainage from the waste facility shall be removed. Replace transfer components
with compacted earth material or otherwise render transfer components unable to convey waste.
To the maximum extent practicable, remove all agricultural waste and associated materialsthat could
negatively affect water or air quality, or pose a safety hazard. Utilize all liquid, slurry, sludge and solid
waste, and soil removed from the facility in accordance with NRCS CPS Nutrient Management (Code
590).
Use precautions (fencing and warning signs) where necessary to ensure that the facility is not used for
purposes incompatible with the facility modification.
Erosion and pollution control
For facilities that receive surface runoff flows including flows generated within the facility footprint, soils
and hydrology analysis shall be completed to quantify expected runoff and plan/design appropriate water,
erosion, and grade stabilization controls.
Revegetate or treat all disturbed areas with other suitable measures used to control erosion and restore
the aesthetic value of the site. Treat areas not suitable for revegetation through normal cropping practices
in accordance with applicable NRCS erosion, grade, and water control CPSs including but not limited to
Grade Stabilization Structure (Code 410), Grassed Waterway (Code 412), Diversions (Code 362),
Mulching (Code 484), and Critical Area Planting (Code 342).
Liquid and slurry waste removal
Agitate and pump all liquid and slurry wastes to the maximum extent practicable. Add water as necessary
to facilitate the agitation and pumping. Utilize the wastewater in accordance with NRCS CPS Nutrient
Management (Code 590).
If the bottom of the lagoon or structure at the actual time of closure will support earth -moving equipment, it
must be scraped. Soil stability for earth -moving equipment shall be determined and documented at the
actual time of closure by an NRCS qualified Engineer, or an NRCS qualified Technician, or a state
qualified technical specialist. For lagoons or structures that are not to be scraped due to documentation
that the bottoms will not support earth -moving equipment as determined at the actual time of closure, the
depth of "agitated" waste material remaining in the lagoon or structure at the actual time of closure may
not exceed a maximum depth of one (1) foot. An NRCS qualified Engineer, or an NRCS qualified
Technician, or a state qualified technical specialist shall verify and certify the sludge has been
satisfactorily removed."
Sludge removal
During sludge removal operations, the integrity of the liner shall be maintained, if one is present. Remove
sludge to the maximum extent practicable and utilize in accordance with NRCS CPS Nutrient
Management (Code 590).
Impoundment closure
Three options are associated with the decommissioning of liquid waste impoundments. Use one of the
following options.
Breach embankment impoundments
Embankment impoundments (those with a depth of water at the design water level of 3 feet or more above
natural ground) may be breached so that they no longer impound water. Liquid sludge waste shall be
removed from the impoundment before breaching the embankment. Grade the embankment material into
NRCS, NC
October 2023
360-CPS-3
the impoundment area, and vegetate the area for another use or retain the embankment if the
impoundment area surface has been sufficiently cleaned so that runoff leaving the site would not be
considered contaminated by the wastes. Remove concrete, pipe appurtenances, and flexible membrane
liners or render the membrane liner unable to impound water. Properly dispose of removed concrete,
pipe, and membrane liner materials. Design stable side slopes and bottom of the breach for the soil
material involved. Three horizontal to one vertical (3:1) is the steepest side slope allowed for a finished
breach slope.
Backfill excavated impoundments
Excavated impoundments may be backfilled so that the area is unable to impound water and may be
reclaimed for other uses. Liquid and sludge waste shall be removed from the impoundment prior to
backfilling. Remove and properly dispose of concrete, pipes,flexible membrane liners, and any other
structures or materials associated with the impoundment. Backfill the excavated area to a design height a
minimum of five percent above the finished grade to allow for settlement. Construct the top 1 foot of the
backfill using the most impervious soil material readily available and mound the fill to shed precipitation
runoff without causing erosion. Incorporate available topsoil where feasible to aid the establishment of
vegetation.
Conversion to fresh water storage
Converted impoundments shall meet the requirements as set forth in the appropriate NRCS CPS (e.g.
Pond (Code 378)) for the intended water storage purpose. Use the National Engineering Manual (NEM),
Section 501.23 for the investigation of structural integrity if the original impoundment was not constructed
according to NRCS standards. Liquid and sludge waste shall be removed from the impoundment prior to
conversion. When it is not practical to remove the sludge from a waste impoundment that is being
converted to fresh water storage, the impoundment must not be used for fish production, swimming, or
livestock watering until the water quality is adequate for these purposes.
Alternate Method of Closure
There are existing lagoons/structures that may be closed by the following alternate method.
This alternative closure process consists of vacuum dredging the sludge and leaving the liquid.
Lagoons/Structures which have a liquid waste analysis of more than 40 parts per million of total N before
sludge removal cannot be closed by this alternate method.
Locations on the lagoon/structure bottom where sludge is 0.2 foot or greater must be dredged. Where the
sludge is less than 0.2 foot in depth, dredging is not required.
Sludge must be removed to the maximum extent practicable on the slopes, but in no case shall there be
more than 0.2 ft. of sludge in the bottom when finished.
The lagoon/structure must be converted to fresh water storage. Spillways, if required under this standard,
must meet the requirements of the Pond Conservation Practice Standard (Code 378) and have adequate
soils and hydrology analysis to properly design structure appurtenances including but not limited to
principal and auxiliary spillways.
Required documentation for the above criteria includes:
A liquid waste analysis performed by the North Carolina Department of Agriculture & Consumer Services
(NCDA&CS) or other accredited lab. The sample shall be taken by Division of Soil and Water
Conservation (DSWC) staff, Division of Water Resources (DWR) staff, or NRCS staff with a WUP/NM
designation as a technical specialist.
A survey of the lagoon/structure showing the bottom elevation and depth of sludge before and after
dredging using a "sludge judge" or other measuring device made for this purpose, on a 25 foot grid, or
NRCS, NC
October 2023
360-CPS-4
closer, if needed to show true size and volume of sludge. The survey and volume computations shall be
signed by a technical specialist with the SD or SI designation.
A representative from Division of Water Resources(DWR), Division of Soil and Water Conservation
(DSWC), or an NRCS qualified Engineer, or an NRCS qualified Technician must verify that the sludge has
been satisfactorily removed.
Fabricated liquid waste facilities
Fabricated liquid waste facilities must be demolished, disassembled, or otherwise altered so they no
longer impound water. Temporarily store disassembled materials such as pieces of metal, concrete, etc.,
in such a manner that they do not pose a hazard to animals or humans.
Bury demolished materials onsite or move material offsite to locations designated by State or local
officials. If buried onsite, cover the materials with soil to a settled depth of at least 2 feet. Backfill finished
grade must exceed the finished design height by a minimum of five percent to allow for settlement.
Mound the backfill sufficiently to divert runoff from the site after the backfill settles.
Dry waste storage or treatment facilities
Remove walls and other structural members or otherwise render the site unsuitable for stacking or treating
waste.
Determine the depth of soil remediation by evaluating the soil at dry waste facilities such as confined
animal housing, feedlots, livestock yards, or composting facilities with earthen floors.
Include laboratory analyses of the soil profile in the evaluation for any nutrients needed to determine the
required depth of rehabilitation. Take soil samples at multiple locations and depths within the facility. Take
one sample per depth interval per acre, of the area being decommissioned with a minimum of three
samples per depth interval. Samples taken for each specified sampling depth interval may be
consolidated into a single set (e.g., three samples taken at the 0-to 6-inch-depth interval may be
consolidated into a single sample for testing). Collect, prepare, and test soil samples in accordance with
NRCS CPS Nutrient Management (Code 590).
Use the results of the soil analysis to prepare a plan to recover the site for its intended use. Utilize the
following site appropriate options, if needed:
• Adjust pH to restore desired crop growing conditions.
• Plant salt -tolerant plants to restore the site to desired crop conditions. Monitor the harvested
vegetation for nitrogen, phosphorus, and potassium removal.
• Select plants and erosion control practices to minimize phosphorus transport from the site and
facilitate remediation of excessively high phosphorus levels.
Although in -situ processes are the preferred method for adjusting the soil conditions, removal of a portion
of the soil may be necessary. Land apply the removed soils in accordance with NRCS CPS Nutrient
Management (Code 590). Grade or backfill the excavated areas to shed rainfall and prevent ponding of
runoff. Where feasible, use available topsoil to aid in the establishment of permanent vegetation.
CONSIDERATIONS
Where practical, conduct preclosure soil and water (surface and subsurface) testing to establish baseline
data surrounding the site at the time of closure. Establishing baseline data can be used in the future to
address soil and water issues.
Where a dense mat of floating vegetation covers the surface, reduce pumping effort to empty waste
impoundments by first applying herbicide to the vegetation and then burning the residue. Obtain
appropriate permits before burning. When conducting burning, take necessary actions to ensure that
smoke is managed to minimize impacts to downwind populations.
NRCS, NC
October 2023
360-CPS-5
Alternative methods of sludge removal may be required where the impoundments contain large amounts
of bedding, oyster shells, soil, or other debris.
Minimize the impact of odors associated with land -applying dry wastes or with agitation, emptying, and
land -applying wastewater and sludge from a waste impoundment by conducting these operations at a
time when the humidity is low, when winds are calm, and when wind direction is away from populated
areas. Adding chemical and biological additives to the waste prior to agitation and emptying can reduce
odors. Odor impacts from land application can also be mitigated by using an incorporation application
method.
Minimize agitation of the wastes to only the amount needed for pumping to reduce the potential for
release of air emissions.
Soil used to fill excavated areas should not come from important farmlands such as prime, statewide,
local, or unique farmlands.
If testing of soil around the facility indicates a need for remediation, use an appropriate NRCS CPS for
planning and implementation.
A breached embankment may detract from the overall aesthetics of the operation. Remove the
embankment and return the site to its original grade.
Disassembled fabricated structures may be suitable for assembly at another site. Take care during
closure to minimize damage to the pieces of the facility, particularly coatings that prevent corrosion of
metal pieces.
Take measures during closure activities to minimize site erosion and pollution of downstream water
resources. This may include such items as silt fences, haybale barriers, temporary vegetation, and
mulching.
To minimize potential impacts to livestock, such as nitrate poisoning, initiate a testing and monitoring
program of nutrient levels in crop products, particularly livestock feeds, harvested from sites of closed
animal confinement facilities.
Consider revegetating using species or diverse mixes that are native or adapted to the site and have
multiple benefits. Native species may be used when appropriate for the site. To benefit pollinators and
other wildlife, flowering shrubs and wildflowers with resilient root systems and good soil -holding capacity
also should be considered for incorporation as a small percentage of a larger grass -dominated planting.
Where appropriate consider a diverse mixture of forbs to support pollinator habitat.
PLANS AND SPECIFICATIONS
Prepare plans and specifications that describe the requirements for applying the practice to achieve its
intended use. As a minimum, include—
• A plan map showing the location and extent of the practice.
• NRCS Job Classification for each planned conservation practice and an overall project job
classification
• A plan view of the layout of the waste facility's existing grade and final design grade including
topographic elevations and locations of survey benchmarks.
• Typical profiles and cross sections of the site as needed. These shall include original and planned
grades.
• Structural drawings including pipes and grade stabilization structures, details, and notes adequate
to describe the construction requirements.
• Requirements for erosion, grade, and water control measures and structures as needed. This may
include details for (but not limited to) Grade Stabilization Structures (Code 410), Grassed
NRCS, NC
October 2023
360-CPS-6
Waterways (Code 412), Diversions (Code 362) Mulching (Code 484), Critical Area Planting (Code
342). For vegetative establishment, list species, planting dates, densities, planning procedures,
amendments, etc.
• Pertinent elevations of the closed facility and excavation limits.
• Number, capacity, and quality of facility and estimate of soil and waste volume to be moved.
• Estimate of demolition quantities (concrete, etc.) to be removed or buried.
• Location of known utilities.
• Requirements for salvage and disposal of structural materials.
• For facilities that receive any surface runoff flows including flows generated within the facility
footprint, hydrologic analysis shall be completed to quantify expected runoff and plan/design
appropriate erosion, grade, and water control designs.
• Hydraulic design documention for any water control structures associated with closure.
• Vegetative requirements.
• Waste utilization plan for animal wastes and soil.
• Copy of the liquid and sludge waste analysis performed by the North Carolina Department of
Agriculture & Consumer Services (NCDA&CS) or other accredited lab.
• Copy of the sludge survey analysis conducted indicating liquid and sludge volumes to be removed.
• Copy of soils sample reports for each application location.
• Copy of PLAT results for each application location.
• Odor management or mitigation requirement.
• Safety plan requirements. Note: Per Occupational Safety and Health Administration (OSHA)
confined space entry protocol, there will be NO entry of personnel into the confined space of an
enclosed waste facility without breathing apparatus or taking other appropriate measures.
OPERATION AND MAINTENANCE
Develop an operation and maintenance plan that is consistent with the purposes of the practice, its
intended life, safety requirements, and the criteria for its design.
The proper decommissioning of a waste facility and rehabilitation of any contaminated soil a waste facility
requires little or no operation and maintenance.
For the conversion of a waste facility to any other use, such as a fresh water facility, the operation and
maintenance will be in accordance with the appropriate NRCS CPS for the intended facility conversion
purpose.
REFERENCES
Rice, J.M., D.F. Caldwell, and F.J. Humenik. Ed. 2006. Closure of Earthen Manure Structures in Animal
Agriculture and the Environment: National Center for Manure and Animal Waste Management White
Papers, pp. 263-282. ASABE. Pub. Number 913C0306.
NRCS, NC
October 2023
360 NC IR Waste Facility Closure: State Permitted Post -
Processing 2024
Jul. 2024
Background: Increased implementation of conservation practice standard (CPS) 360 Waste
Facility Closure - lagoon closures, the corresponding number of CPS 590 Nutrient Management
plans, and challenges with finding available land for direct application of raw, lagoon materials, has
created opportunities for the development of value-added, post -processing of lagoon closure by-
products. In North Carolina, state, federal, and non-federal partners have provided funding for the
development of technologies, methodologies, and systems for utilizing manure and raw lagoon
materials, and creating market -viable, value-added by-products. North Carolina has traditionally
been very pro -active in establishing guidelines and regulations for the handling of animal manures.
Therefore, operations involved with post -processing of lagoon materials should be approved by and
working under state regulatory and permitting authorities (e.g. NC Dept. of Environmental Quality).
These types of processors will be referred to as "state permitted post -processors".
Conservation Practice Standard (CPS) 360/590 and Role of State
Permitted Post -Processors:
When state permitted post -processors are part of a CPS 360/590 lagoon closure
plan/design/implementation (i.e. all or some of the lagoon materials are utilized by a post -
processing facility), the CPS 360/590 plans shall include:
1) Registered name of the state permitted post -processor and facility location.
2) State agency with approval and permitting authority (i.e. state permitting agency(ies));
include permit identification if applicable.
3) Planned input volume and characteristics of CPS 360 generated materials.
4) Expected final product characteristics and quantities.
When post -processed water is a product of an approved and permitted post -processing
methodology, water quality shall be tested by an approved lab. When the water's total N is less than
40 ppm and all other tested compounds/elements are below recognized hazardous levels of
concentration, such post -processed water may be utilized to refill lagoons that are approved for
conversion to fresh -water storage. This shall also be documented in the CPS 360 design
documentation and the CPS 590 nutrient management plan.
Planners shall ensure the identified post -processors are under current purview of state regulatory
agencies. All current CPS 360 and CPS 590 criteria remain applicable and are expected to be met or
exceeded. Under these conditions, the use of state permitted post -processors are an acceptable
component of CPS 360/590 plans.