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Home My WebLink About640067_Maps Closure_20231113Date: 09/09/2022 WASTE UTILIZATION MAP r +(s):SWIFT CREEK HOG FARM Field Office: NASHVILLE SERVICE CENTER t: NASH SOIL & WATER CONSERVATION DISTRICT Agency: MRCS Assisted By: John tong State and County. Nash County, North Carolina Lega Description: Tract 7467 Legend Prepared with assistance from USDA -Natural Resources Conservat-on Service TRACTNBR ® Ditch— Buffer 25_Ft '467 Pro perty_Lines_Buffer_25_Ft Well ® Non —Farm _ Residence _Buffer_200- f t ® Well —Buffer 100_Ft Roads 0 330 660 1.320 1.980 Feet Streams Date: 09/09/2022 WASTE UTILIZATION MAP r,' lfs):SWIFT CREEK HOG FARM Field Office. NASHVILLE SERVICE CENTER NASH SOIL & WATER CONSERVATION DISTRICT Agency_ NRCS Assisted By: John Long State and County: Nash County, North Carolina Lego, Description- Tract 3681 Lpry4nd Prepared with ass stance from USDA -Natural Resources Conservation Service T jTNBR Ditch_Buffer_25_Ft 3681 Pro perty_Lines_Buffer_25_Ft ® Well ® Non_ Farm_ Residence_Buffer_200_Ft ® Well_Buffer_100_Ft 0 330 660 1,320 1, 980 Feet Uate: Ubr1512uz.5 WASTE UTILIZATION MAP Client(s):Swift Creek Hag Farm Field Office NASHVILLE SERVICE CENTER District: NASH SOIL & WATER CONSERVATION DISTRICT Agency: NRCS Assisted By: John Long Stale and County: Nash County. North Carolina Le, ascription- Tract 3664 1Ld •" -• •_••" ••,• 0 330 660 1.320 1,9$G Well —Buffer 100—Ft. Wetl — Streams — Roads Nash Date: 0510812023 WASTE UTILIZATION MAP ' ;lient(s)- SWIFT CREEK HOG FARM Field Office: NASHVILLE SERVICE CENTER Nstrict: NASH SOIL & WATER CONSERVATION DISTRICT Agency: NRCS Assisted By: John long State and County. Nash County, North Carolina bg salption: Tract 8236 0 Well Prepared with assistance from USDA -Natural Resources Conservation Servic Streams 0 330 660 1,320 1,980 Roads Feet Date: 0510812023 WASTE UTILIZATION MAP :Gent(s). SWIFT CREEK HOG FARM Field Office: NASHVILLE SERVICE CENTER )_strict: NASH SOIL & WATER CONSERVATION DISTRICT Agency: NRCS Assisted By: John Long State and County: Nash County, North Carolina eg scxiption: Tract 8235 Prepared with assistance from LISDA-Natural Resources Conservation Service — Screams 0 330 660 1,320 1,980 Roads Feet L cu A y. CV E {� M L O (9 a` L co ~ N C> N 8 a r � p V 1 — • Ol � Q in O N C 3 O GS CD T ftF J N m E m m m E C m � W c C a 7 Q J C U n � �Eom � U 2 a c� a m � c y G N @ -2 C C C m O 00 m _ O t5 m Q� w=�E vmE,co c LL -i Lu U m i C> R. a Q LL v m a W E m a d m U Z � � �r 2 m �mW m � a m � C b � S} m ro � z �a W m w m � v +6 m a c C m � rn K m m m q a m n C W � E va m m N L pC V V 6 m O II � C W m 0 O Q _v a� N 4 c O W n C ti m o m c m N � ID E c_ N LM YI Q W �+a C }, Qp O Q � m � V_ej m e N W m {0 m m LL L Q 0,6 N a o L W r€ N m i O R N � 0 y X d N 19 = d E `m m � a m a _ c N O Vl � W m m m 0 L AC'KNOZ1-[.Eli ,E.N-IENT OF THE POTE\TIAl, IIMPACTS ON .A SITE FROM APPLYING LAGOON SL[Ji}GE As part c-,f either a lagoon closure operation or on -going lagoon n7aintenanee. the attached Flan has been developed to apple sludge to the following areas: Tracts & Field lumbers: T,o_cf 36at5 F.rtd15 43 1U, 718,,7 While using animal «aste as a source of nutrients for crops in lieu of inorganic fertilizers is an ecological] sound practice, producers should be aware that sludge that accumulates in a lagoon 177av have high concentrations of nutrients and.'or heavy metals. Accordingly, the quantih of phosphorus and micronutrients in the material to be applied may exceed the fertility requirements of planned crops. Metals. High concentrations of metals in the soil can impact crop Lm'.)wth or }Melds. The application of lagoon sludge has the potential to significant)}r increase the concentration of metals (particularly copper and zinc) in the soil. ICSU and l'CDARCS recommend that alternative sites for waste application be sought when soil concentrations of zinc (Zn) exceed 142 lbs/ac (Zn-1 of 2000) or copper (Cu) exceed 72 lbs'ac (Cu-I of 2000). A Cu-I or Zn-1 of 3000 is recognized as a critical toxic level for some crops. For peanuts, alternative sites are recommended when the Zn-1 is 300, and a Zn-I of S00 is reco2ni7ed as a critical toxic level. Producers should be a« are of the post -application Cu and Zn concentrations predicted on the site.4t planned for sludge application. Additionaliv, soil pH should be maintained at 6.0 or abn%-e to minimize risk of toxicitti . Phosphorus. Phosphorus (P) concentration in lagoon sludge may be high. Because P adsorbs onto iron}, aluminunn. and calcium, the soil can bind and store excess P. 11'her7 P concentrations reach higher concentrations. there is an increasing potential for P to be transported offsite and become a pollutant of surface seaters. This transport may occur through soil erosion, or as a soluble fonn in surface runoff or leaching. An assessment of the risk: for P loss to surface water is required as part of a nutrient management plan for pem7itted operations or those receix in federal or state cost -share assistance. If the potential for P transport offsite is high~ then future application of animal waste may not be allowed in a nutrient management plan. Producers should be aware that applying ]aeoon sludge may limit the ability to use the site for future animal «aste application. Accordingly-, applying lagoon sludge to fields that are planned for future waste application as part of a nutrient management plan is not advised. I understand that apj) wing mac'n•ott m ients or iniei-onuwierits at rates that signifrcanth- exceed the expected croj7.removal could limit the funwe use of tlae field as a it aste applications site. and inn some cases. nsegotiveh• impact fitowe plant gross th, I t-olrtnstarals- agn•ee to apphv sludge to the fields identified above that I oitw or operale according to the attached mm-ienst management plant or lagoon closure plant. (`Both Imidott'sser aard.ja)-mev"olmrator must sign.) �o2/—aka t n.x Date Fanvuen-- operator* Date CNM1' Dn-chp,itenr and hnj l_m-,ntarion C'hecMi t tiRCS. NC MaN 2009 'R,-cz�:d Feb 201- -, p h rlau r��: Cy,t C%.z File 1eh ��i� / ` r. ACKNOWLEDGE`-1ENT OF THE POTE3NTIAL. IMPACTS ON A SITE 1=RUM APPLYING LAGOON SLUDGE As part ofeither a lagoon closure operation or on -going lagoon maintenance. the attached plan has been developed to apply sludge to the following areas Tracts & Field Numbers:41 10 While using animal waste as a source of nutrients for crops in lieu ofinorganic fertilizers is an ecologically sound practice. producers should be aware that sludge that accumulates in a lagoon may have high concentrations of nutrients and/or heavy metals. Accordingly, the quantity of phosphorus and rnicronutrients in the material to be applied may exceed the fertility requirements of planned crops. Metals. High concentrations of metals in the soil can impact crop growth or yields. The application of lagoon sludge has the potential to significantly increase the concentration Of metals (particularly copper and zinc) in the soil. NCSU and NCDARCS recommend that alternative sites for waste application be sought when soil concentrations of zinc (Zn) exceed 142 lbs!ac (Zn-1 of 2000) or copper (Cu) exceed i? ]bstac (Cu-I of 2000). A Cu-1 or Zn-1 of 3000 is recognized as a critical toxic level far some crops. For peanuts, alternative sites are recommended when the Zn-1 is 300, and a Zn-I of'500 is recognized as a critical toxic level. Producers should be aware of the post -application Cu and Zn concentrations predicted on the sites planned for sludge application. Additionally. soil pH should be maintained at 6.0 or above to minimize risk of toxieity. Phosphorus. Phosphorus (P) concentration in ]a4toon sludge may be high. Because P adsorbs onto iron. aluminum, and calcium. the soil can bind and more excess P. ��'heih P concentrations reach higher concentrations. there is an increasing potential for P to be transported offsite and become a pollutant of surface waters. This transport nlsy occur through soil erosion. or as a soluble form in surface runoff or leaching- An assess3lient t)f the risk for P loss to surface seater is required as part of a nutrient management plan f,,r pennitted operations or those receiving federal or state cost -share assistance. If the potential for P transport offsite is high, then future application of animal waste rna�, not be allossed in a nutrient management plan. Producers should be assure that applying lagoon sludge may limit the ability to use the site for future animal siaste application. Accordingly. applying lagoon sludge to fields that are planned for future waste application as part of a nutrient management plan is not advised. 1 understand that aj)j lhving macromar•ierrts or nricr'orrittrients at rates that significarttli. exceed the c.spected 0-017 r errrot•a1 could limit the future use of the field as a waste application site, arrd ill some cases, negatit•el} impactfitture plant growth. I volwitari1v agree to apj)ly Sludge to the fields idemif ed above that I oit•rr or operate according to the attrrclred rrtrtrient nrcrrragerrterrt plan Or lagoon closure plan (*Both landowner- and farnier'�operator• rrrrrst Sign.j 7•rrev* Date Favorer Operator Date C'\�ti' De�z1.pt7,r[?[ 1I](] If77}?]�mei7tatiort Check]i�t NRC•S. `C `]a% 2009 [Rerir.J feb?o17--A rkl mat: fig: C'�MP Ca,e F-;l �f } p } e ] _ .J1! S;tina.urt Pa-:R:�'!Ired r) :iACKNOWLEDGEMENT OP THE POTENTIAL IMPACTS O': A SITE FROM APPLYINNG LAGOON SLUDGE As part ofeither a lagoon closure operation or on -going lagoon Maintenance. the attached flan has been deg eloped to apple sludge to the followincy areas: Tracts & Field 'umbers: While using animal %vaste as a source of nutrients for crops in lieu of inorganic fertilizers i• an ecolo('icall} sound practice, producers should be aware that sludge that accumulates in a lago.)n rna%. ha\ e high concentrations of nutrients and:or hea\}y metals Accordingl)-. the quantity of phosphorus and micronutrients in the material to he applied maS exceed the fertility requirements of planned crops. Metals. High concentrations ofrnetals in the soil can impact crop (Frowth or yields. The application of lagoon sludge has the potential to signilicantiv increase the concentration of metals (particularly copper and zinc) in the soil. NCSU and NCDA,-CS recommend that alternative sites for waste application be sought when soil concentrations of zing. (Zn) exceed 142 lbs/ac (Zn-I of 2000) or copper (Cu) exceed 72 lbs-ac (Cu-1 of 2000). A Cu-1 or Zn-1 of 3000 is recognized as a critical toxic level for some crops. For peanuts. alternative sites are recommended when the Zn-1 is 300. and a Zn-1 of 500 is reco��njzed as a critical toxic level. Producers should be aware of the post -application Cu and Zn concentrations predicted on the sites planned for sludge application. Additional]\-, soil pH should be maintained at 6.0 or above to minimize risk -of toxicity, Phosphorus. Phosphorus (P) concentration in lagoon sludge may be high. Because P adsorbs onto iron. aluminum. and calcium. the soil can bind and store excess P. \\'hell P concentrations reach higher concentration,, there is an increasing potential for P to be transported offsite and become a pollutant of surface seaters. This transport maY oceu; through soil erosion, or as a soluble fon» in surface runoff or leaching. An asse'sSmenr of the risk for P loss to surface water is required as part of a nutrient management plan tier permitted operations or those receiving federal or state cost -share assistance. If the potential for P transport offsite is high, then future application of animal waste may not be allowed in a nutrient management plan. Producers should be aware that applying lagoon sludge may limit the ability to use the site for future animal waste application. Accordingly, applying lagoon sludge to fields that are plarmed for future waste application as part of a nutrient management plan is not advised, 1 understand that oppl3'ing macronutrients or at rates that sign ficotrtlr• exceed 1k; e.vj?ected crop removal could limit the. future use of the field as a waste application site, and iti some cases. negatively impact.ftttt)re platrt 9/-0117l1. 1 i•olruttar-ill' agree to apple• sludge to the fields identified above that 1 own of operate according to the attached nutrient management plait a- lagoolt Closure plan. ("Both lcmdowner anal farmerlope!•atol• ))rust SI231. j " Date Fat-ntel', Operator'` Date C'NM11 Dza elopmtnii amid lrnplemremation ChecIrditr NRC S. `C \iati 2009 RtniTed Feb 201 +--Appropriate 6-)r C NMP Ca-: Fm,e Fell' 201 Sis imz:s r, E'a ;e P ACKNt)WLEDGE )IEIT QFTHC PO"I ENl IAL INIPAC TS OVA Sit L FRO)�l APPLYING LAGOON' SLUDGE As pan 111 either a lagoon Same operation of mygoing liigwn 111;in1tCnanCe, the attached plan has been det eloped to applt SIL1(t ,e to the areas: Tract; & Field \°unrher;: i �.z.2 E--gr.3��(1.5��7��-.i " bile tlgng animal "one a% it soma of nwiJents for crops in lieu of inol-L'allic fertilizers is an LctYlogicallt sound practice. ;ti';!:3_.mti sholuld lie aware that '�]udge that acculllulates in a lagoon may hate high concerltriidow tit ilt•.ments and/or- ]leant" metals, Accordinglt. the quantity of phosphorus and micronumems in the mwerial to he applied may eNCeCd the 911dity requirements ot'planned Metals. l-litigh concentrations of metals in the soil can impact crop &Jrott th or vields. The application of lagoon sludge lilts the potential to dgrdficantly increase the concentration of mends (particularly copper and zinc) in the soil. \CSV and \'CDA&-C S r•ecoillrllenil that alternative sites for wane application be sought when soil concentrations of Wnc (7n) exceed 142 lbs ac (Zn-1 of 000) or capper (A) exceed 77, IS ac {Cu-1 of ?000). A Cu-1 or Ln-I of 000 is recognized as a Weal toxic let el for Borne crupi For peanuB. allenimin e sites are recori mended ;then the Zn-1 is 300. and a Zn-I of 06 is recognized as a critical ionic level. Producers should be a" are of the p.st-applicadon Cu and Zrl concentradons preziO& can the sites planned fir Sludge application. Additionally, sail pli shojkl he manitahiml at 6.0 or abo c' to minimi7.e rlslk of toxicity. Phosphorus. Phmphorus i P 1 concentration in lagoon sludge may be high. Because P adsorbonto lr'On. alunllnlrni- -!nd calcimi. the soil Call bind ailil swre mess P, \\ hen P concerinstions reach li gher concentrations. there it all increasing potential Qr- P to be transported offsim and become a pollutant of' surface water;. This transpoi-t relay occur through ski erosiow or as a soluble form in surface runoff or leaching. An assessment of the rise, for P IOSS to Surface t'.ater IS required as part or a nutrient manageriml plan filr permuted operations or these receiving federal or state comhare assistance, if the potential for P transpor-t offsite is hiygh. then future application of amnia] I,-Ljste flat' not be allowed in a nukent management plan. Producer: should he aware that applyin., lagoon sltld<ue inat' NO the abihtt €0 use file site for future animal waste application. Accordi gbg applying lagoon sludge to fields that are planned for future waste application as part of a nutrient management plan is not adt.ised. 1101dowa11d 1114-11 aplxli'in M(10'01111!ricirh or 1i11C'1'c7111l11'lE'Fll$ (11 1Y1!Cs 111('1i siz11llic:(11111i e-t,cecgd thcc r.tpcctfd crol? 1'c;llroi'c11 coldd limit the lutlrl•e use al ill(, lield a.s a i, aste c11)p1icc1rio11 site. an(I in Some Ca1m�es, 1 CgUtll'C'11 in1l)(IC'1,lillilre111:111! a1'U c'dl- I t-olmll(lrilr- agree to (1pp1t's11r11gc to the- licldc idemrilicd ahow tl a I ouni or o1hraw accordin-g to the atla0wel marlellt or lagoon c'1 uire lVoli, I *Both lando"ner and lal'11w),ol1 o,olor 11111.sl sign.) - DOIC 1=ar111er Ol)C1-11tf1J-k:------�---�- .+�, t ---- -- 1C K7' 0ONYLLDGE)IEN'T OF 7 HL POTENTIAL 11IPACTS ON A SITE FRONI APPLYING LAGOON SLUDGE As pan cif either a lagoon closure opentlon or ongoing lagoorl maintenance. the attached plan has been developcd to apply sludge tet the fctlkm ing area;: Tracts. cC Field \ umher,:--- "Ide using animal Taste as a source ofntltriems Ar crops ill lief€ otillorgalliC tertih4CI's i, all ecolo+slc Hy sound practice. producers should he aware that sludge that aCCtlmtrlates ill a la+gooll may have high concentrations of nutrients and/or heap I metals. Accordinyjl;� the quantity of' phosphorus and rllicronubems in the rnmerin] to he applied may exceed the fertility requirements of planned crops. \dawls. High concenustions of inetals in the sod can irnpam crop grtF"S or A fields The application of lagoon sludge has the potential to si4�niticantly increase the concentration of metals (padcularly copper and zinc) in the snit. \*CSL' and \CDA&CS recommend that alternalive site: for waste application he sou`L]lt v.-hen soil coilcerltratloll� of, zillc (7_1':) exceed 142 lhs ac tZn-1 of 21TYt) or copper (Cu) exceed 72 IS ac (Cud of?t.itl(1r. :k Q-1 oI- Zild of, 000 is recognized a> a critical toxic ]e el for s.?me crops. For pearlLits, alteI wive sites art' recommended when the Zil-1 is 00. and a Znd of 00 is recuplized as a critical toxic le%el. Producers should he antial-e of the post -application Cu and Zn concentrations predicted cm ih: sites planned for sItldLle application. Additionally. )i] pH should he maintained at 6.0 or aho%e to 1111111n117e ric", CFt tip.\ll lt�'. Phosphorl1S. Mlosphor us f P1 concentradon lrl laymm dodge may, he 133O. 1'St;caWC P adynbs onu> iron. alunlir.um. aMd calciulll. the snit can bind and store e.xce>, P. lt'hen conctnuntlons reach higher concentrations. there is all [nCI'euslny� potential for P to be transported offsite and became a pollutant of surface waters. This transport may occur through soil erosion. or as a soluble form in surface runoftor leaching". An assessment of the risk for P loss to surAce water is required as part of a nutrient management pI. I fit permitted operations or those mceii-ing federal or state cost -:hare assistance. If tile pcnential for P transpori offsite is high. then future application of animal waste ma\ not be allowed in a nutrient management plan. Producers should he aware that applyll-q-, lagoon sludge may limit the ability' to use the site for fu11-€1'e animal Taste application Accordingly, applying lagoon sludge to fields that are planned for future waste application as pare of a nu€rtent management plait is not advised. I inidc*mand that N;jv rrg nrctcrmurl iews a- micr•crrrim eats at rates Hurt sigrrilJcarttit c.�'cc�°d the c.iyn,eted crop removal could limb the 41nwe trse ol'the .lield as ct llvsle applicatiorl site. and ill sortie c(OCS. trcyfcrti1e11 in1pc1ct fillure Ant gro?iS. I voluniarill- agree to;rppll slrrc(gf' to the Jiehb idcrrtified crbow that I mvii or operate ,ccor�dirrtJ to the attached rrtrtrit'rrt rtanooerrrerrt I?larr or la,omi clnstwe plan. ("Both landowner and farmer/operator musl sig,11.) O .rre Data I'arnwr• 01)orwor* — _ !Dart' — VP ! �:\-,-ioilil2�-11' i:f?fir t i,i ?f�(I�: ,r :,�<�.. t �t' �i+� - '�?'•'i=iC In C.' mP C a' '.-ii: i ii,'uEil:itlmi ... t ek -Ii; f P. AC_ KNOWLI`I)GE_NIENT OF I HE PO -I ENTIAL I NIPAC-1 S ON A SII-E FRO.N] APPLYING L AGOO\ SLUDGE A�, Hari of either a lagoon closure operation or on-gloin`, la -goon €mt€meriamte. the attached plan has been developed to apple sludge to the Allo" ing areas: Tracts S, Field Numbers: _1 -3670 �- r, zr-�Yr i 6E��- _t1_}.Lzr 131y, 13,1_7 "Ide usinM animal "ante as a source of nutrients 161' crops in lieu of inorganic fertilirtrs is an ecologically sound practice, producers should be aWai'e that sludge that accumulate$ in a lagiloon rnati have lli,,=h concentrations of nutr€ems andQr heavy €Metals. Accordimdv. the yuentity of - phosphorus and micronwhems: in the material to be applied may exceed th. fertilit\ requirements of'planned crops. )+Ietals. I10i concentrations of metals in the sail can impact crop ��ro�t th or yields. The application of launon sludge has the potential to significantly increase the concentration of metals (particularb, copper and zinc) in the soil. NCSC' and \CDA&C'S recornniencf that alternatk e sites fir waste applic K1 be sought When soi: content- ti�'n� of Zinc (Zll) exceed 142 lb�,tac tZml of 2000) or copper (Cu) exceed 72 ihs'ac (Cu-I of 2000). A Cu-I or Zn-I 4 3[}f}'r is recognized as a critical toxic level for some crop;. For pearnits, ahernative sites are recommended when the Zn-I is 00. and a Z-n-I of zst`1 is recognized as a critical toxic Ievel. Producers shmdd he aware Of Be p,,;t-gvHcatinn Cl, and Zn concentrations prediewd on the sites planned for sludge application. AdditiclnalIv. soil r H shOUld he manttained at 41) or abut e to minimize risk of toxicity . Plygphort€s. Phosphorus A concemration in Qoclrl ltldue may be high. Because p ad,voi-bs onto iron. ahnninum. and calt'4im the soil Cali bind hRd stole &we,; P. "Ten P concenum6ons reach higher Loncenvaticins. there is an i€icreaviI g polemil fclr P to he tranVorted oRlde and become a pollutant Of;urface waters, This transport mat' occur tinvugh sail ercFsion. or as a soluble form in surface r-t€nof'for leaching. An assessment of the risk for P loss to surface water is required a; part of,:: nutrient management plan Rir penN ued operations or those recek ing federal or state cost -share assistance. If the potential Ir P uanspor-t offshe is high. there future application of aldriml "ante rnapnot be allo"ed in a nutl-tent management plan. Producers should be aware that applying lagoon sludge may knit the AN- to use the she for future animal "ante applrcauon. Accordingly. applying lagoon sludge to fields that are planned for ftrlt€re \va.te ailAiCat€on as pan of a nument management plan is not advised. 1 urr,A°rsnmd that clphlrrng madras mierrts or'rrricmrrri 1mrs at r(1lc's that sigtri/icarrtls m.cced 1/1, c.rll� ctc�ci rrol,) rc}rtroml couhl lirrrit the hairre me of thekhl as a waste apl�licali<ifr silt}. card in 1�0111c, e cr,s<'e. rrc gaativcv itlrlrac t_Iirture lAni gro"A. I l,olrurtarill- agree to crpPll sir Lc , to the lit ldi ulcmr fiat` ahoiv that i oil /I of ujvrate acc ir•c Ng to rite atmchni trtrtt'ierrt rrrWUWe>rtrNrt Irlirlt W' lagoon Closur_c plan. (Voth lairCl[D'itwer and lutmer:yl nvmr trrrrst sym ) j -z/--2 j Dale ---'N—L- Darc TWO iU.cll:... t cc MnOmo inn. to C NMF C n - }'Sec t iC.-.<.,-..._.. -Y 1 ` 2. ` - � .ACKNO« LEDGEMENT OF THE POTENTIAL IMPACTS ON A SITE FROM APPLYING LAGOON SLUDGE As part of either a lagoon closure operation or on -going lagoon maintenance, the attached plan has been developed to apply sludge to the following areas: Tracts & Field lumbers: { 37I� F:�(� t 3�yt While using anirmal waste as a source of nutrients for crops in lieu of inorganic fertilizers is at. ecologically sound practice, producers should be aware that sludge that accumulates in a lagoon may have high concentrations of nutrients and -or heavy metals. Accordingly. the quantity of phosphorus and micronutrients in the material to be applied may exceed the fertilih requirements of planned crops. J Metals. High concentrations of metals in the soil can impact crop growth or yields. -I-lie application of lagoon sludge has the potential to significantly+ increase the concentration of metals (particularly copper and zinc) in the soil. NWSL' and NCDA&.CS recommend that alternative sites for waste application be sought when soil concentration; of Zinc (Zrl) exceed 142 lbs-ac (Zn-I of 2000) or copper (Cu) exceed 72 lbs`ac (Cu-1 of 2000). A Cu-I or Zn-I of 3000 is recognized as a critical toxic level for some crops. For peanuts. alternative sites are recommended when the Zn-I is 300, and a Zn-1 of 500 is recognized as a critical toxic level. Producers should be aware of the post -application Cu and Zn concentrations predicted on the sites planned for sludge application. Additionally, soil pH should be maintained at 6.0 or above to minimize risk of toxicity. Phosphorus. Phosphorus (P) concentration in lagoon Sludge may be Irigh. Because P adsorbs onto iron. aluminum. and calcium. the soil can bind and store excess P. Niter P concentrations reach higher concentrations. there is an increasing potential for P to be transported offsite and become a pollutant of surface waters. This transport may occur through soil erosion. or as a soluble form in surface runoff or leaching, An assessment of the risk for P loss to surface water is required as part of a nutrient management plan for permitted operations or those receiving federal or state cost -share assistance. If the potential for P transport offsite is high. then future application of animal waste may not be allowed in a nutrient management plan Producers should be aware that applying lagoon sludge may limit the ability to use the site for future animal % aste application Accordingly, applying lagoon sludge to fields that are planned for future waste application as part of a nutrient management plan is not advised. I rl+tde)'staild that applying nlaci•0111111'ients or nricrolrtttrients at rates that sign jicantly et-cced Mc. expected 0-01.) 1'emoval could limit the /unite Use of the field Cis a waste application site, and in .some cases, negativelt- impact futtir<° plant gi-owth. I r'oluntari1v ag ve to apply sludge to t1ic. fields ideirtlfied above that I own a• operate according to the attached nutrie)rt management picitr Or lagoon clostwe plait (*Botlr leirrdoii ire)• aitd fai-t)l(,n'operatoi- nrtist sigrl.) P1 X Date Farnrcis Operatnr'° Date Dv elop;mt�ni and Implem.niant-ri Cht'Ah';t 'RCS. tiC- 1'. 20r19 (}wired 1'eb 201 - i i): - lr!aii tip' ( Nitl, Ca« }lie D,::k1:�1CF1ia.iCi^ } 20i 7. ,Y_i.ai... t'u_2 JZ?:�tI!_:Ur ACl:NONVLEDG1=.* ENT OF 1 HE I'01-E" TLAL IMPACTS ON .A S1-1-1=, 1-ROM Al"PLYING LAGOON SLUDGE A; part WWI: a lagoon closure tTewuiolt of on -going lagoon inuintenance, tilt. attached plan her, been dC\ ebbed to apply �ZILICIQ to the Wo" ing mews: Tracts & l'ield \ ur nhers: T- Y'23 3 F-2 "Me Using animal hove as a source of nutrients far croly in lieu ofinorwinic 1cndaeg is ail aeWogically sound practice. producers sllM he away that sludge that aCCUmtllateS in a lagooll may ha%e hQh concentrations of ntrtrienu anrl%or heavy meM6. Accordingly-. the quantity, of phosphorus and n ieronutriellt; in the nimer•ial to he applied may e.xceecl the fer-tilit\r requirements of planned crop:, \Metals. l- gh concentrations of nietals in the soil call impact crop grow the or yields. Tic application of lagoon sludge has the potential to sigplificantly increase the concentration of memis fpartrcularly copper and zinc) in the ,ore. \CSL' and \CDA&-CS recolhllnelld that alternatixe site, Ar waste application be sought When sail concentrations of line (Zn) exceed 142 IS ac (Zn-1 of 3000) or copper (Cu) exceed 72 lbs ac (Cu-1 of' 2000). A Ctl-1 or Zn-1 of M) is rect.gnized as a CI'li e& toxic lekel for' some crt)ps. For pedrlllts. alterllalk e sites are reconnnended when the ZIA is 00. and a Z11-1 of 500 is recognized as a critical toxic l vel. Producers shndd be aware of the powt-application C,u and Zn concentrations predicted on the sites planned for ,Judge application. .adcliti+.�nall�". soil pl-I should be maintained at 6.0 or aboe to minimize rk!,: oftoxicitt. PhusnKru,. Phosphorus (P) concentration in lagoon slud��e may' be high. Becau e P adsorbs onin iron. aluminum. and ealcitrrrt. the soil can bind and store e\ce:; P. l%ghell P concentrations reach lugher concentrations. there is an increasing potential for P to be trarlymned t}ffsite and beanne a pollutant of surface "aters. This transport ma; occur through soil emsbri. or as a soluNe forth in surface runoff or leachin". An assessment (if the rise: for P loss to surface .pater is required as hart of a nutrient managernent plait !or penldned operations or those receiving federal or state cost -share assistance. if the potential tier P transim oflite is thigh. then future application of ailtlllal «'aste may not he allowed in a nutrient management }elan. Producers should he aware that applying lagoon sludge may limit the abihq- to use the site for future animal waste application. AccordinYg,ly, applying lagoon sludge t,, fields that are planned for f iture waste application as part of a lllrtriCnt mailagernent plan is not advised. I rltrclel:cland thai upl)ll'ing 1iu1crc111uti'ic lrts 01' 1trlct cjtrtrirrettls at ralus Inert srgl!rfrrrrlrrJl c,.tc(,Cc/ 1/1c' cxI)e0ed droll remoiwl wield liluft the ftami tlse Whe Jielr! as a ""sic a11p1rccrti0lr site, cllrcl rut �01ite CUSCs, lw'!, cltiivc v imoac t J11tlt1re 1)14111t grotr'tlr. I t•011111taril'v agree to a11111v sludge• to Ihc? fich-A idem fic el c1J oiv that I own 01' op['raic ClC'COJ"c1171� to the ctttached 11r11riclit 11rf111clt�PlYlEi1! 1)J[111 or !a owi c•K viv 14am r Moth landonwer and limner ol2erat(r tints, Sig,,.) i Dare 1"arincl,Om,ratrwr� NRC 1. \�- ACKNOWLEDGEMENT OF TI-t;r P07 EtiT1AL IlNIPAC7 S 0", A SITE FROM APPLYING LAGOON SLUDGE As ])(l['[ Of CitlWl' a ]a`(l)t111 CIO-SLIN 01)erati0ll Or laL'I_0I1 Ilia liltell ance, the attached plan has been de\ eloptA to apply' :ludae to the filllowinLl area;: Tracts Field NLimhel'ti: While L151nL anilMal W\ ]Ste aS a SolurCe Of IlUtrleiltS fllr Ck"U])S ill IleLi fel'tihiers is an eCOlU-'ICall\' SOUnd practice. flrl)(ILICUS ahc)Llld be a\\are that SlUd4ie that acClllllulates Ill a las k)oI1 illal' lhaVe h!2h CC)IlCellti'atiOlIS Of 11L1trielltS alld/or }lea\"\' Illetals. Accordingly. tll2 C]Lla(lilty of p}loSpllorLl-S and [Micronutrients ill the :Material 1;1 be applied may exceeci tilt felTilit\ requirements of planned crops. Metals. High ei)neelltr q OilS Of Illetals in the soil call inl])act CI-01) `�rL�\\th c)I- \'I Idw. The appllCal1C�11 OC oil SILkIlue has the potential to Si-?n]f1Ca11t11' 1iCl'ea5e the Concentrationof Ill,-ials 1parlicula1-1\ Copper and zinc) Ill the soil. \CSl ' and NCDA&CS reCOIllmend that alternative sites for waste application be sought \s:heil Soil Colleelltratiotl; ofyin; (7_ll) exceed 142 lbs ac (Z(1-f of -2000) or Copper (Cu) exceed 72 lb: aC (Cu-I of 2000) A Cu-1 ()r Zn-1 Lit "000 is reco f,111`l_ed as a Critical toxic lL\ ei for sollle CI"Opp. i t1(' peailElts. al€ernanve sites are reCO Mllleilded \\Alen the Zn-1 1S 3()0. alld a Z11-1 0 �0(i i. l'eci,,lized a: 'a critical [L7xic In el, f rodLlceB Should be a\\ -are of the post-tlllplieatic,I1 Cu &Ild Zn concewrauons predict ,d tail the sites planned for Sludge application Additionally. Soil pl-i -Should b- maintained ,zt 6.0 or above to nlininlize risk oftoxicity. }zhE�S}atli1rl3S. }�nos1711OI'L(S (1P) concentration Ili la�E-,00n Sllid`�t' 1Maiv be Ilt`h, �el aElse [} adsorb oil to Iron. alL11111nL1i11. al1Ci ealc:iL:ill. tile ,-Oil Cltll Mild and siore excess P. L\ hell In COiIC[ ntl"atiollS reaJl hl<,hL(" Concentrations. there is an 111creaSill`' Potential f q- f [j) be transported off-lrte and beCO111 ° a P011iitallt Of'SLlrface \\'atel"s- i }11S tra[lspoi-t IMa\` 0-t`%Llr tlll'c)tl0h i{)]l trllsWil. 01' as is f0I"111 Ill �,Llrface rLMOff 01' leaching. All assesslMent of the rill. COT f IOSS to sUr}caCe W itel" iS re(]LIII"ed as part of a ilLEtl"12I1t management }lla[l fly;' pernhitted operations or those receiving, federal or state co,t-:hare assistance. if the potential for P trans})ol"t Offsite is 11i211. [hell flltUre application of aninial waste may not be allowed in a nutrient management plan. PI.00ILI 'S should be aware that apply inks la(20011 slud�,e ilhav 1111111 the ability M LI e the site for filtM-e all' lllal wa-ste application. AccordinylN. applying la"oorl sludge to fields that are planned f01' future \waste application a-, part of a nutrient mana�tement plan is not advised. l 1rllrl{'i'.+tf131S1 111a, c1p1'li'iiia lilciC,"�1)ilrti'!C'111,\ oi' lillC'1'o111i.'1'iCFIt.S c1r 1'atc•:� 111M sioililicrr,i,11' c'xce( cl rile c _rl.ccrcd crop i-L-moval rmild limit the lunire 13c of the heir/ ac rt 13 r,stc r,ppli4:viti0ll site. crllil ilI \o11IC CtijC'C, IlC' [1!!1'r�ll' !llllxf,r`t 11111wo pant 2Irvl,11, 1 1•oluntal- ll (1,�,r<'c to a,+)plv sltirlge to tlrc lic'lcA iclemiliccl (ibol-c tiler, 1 o',,vi or opeivie accoi•cl,ing to the attotI e')11rrr1•ient iiIanagenicill i hul Or ICI.-C"' I c-lo-SIff-e plain t "Both 1{r10011,ter m0 / inlic I' ol)c', arcu',1nw sirz�il.� 77 0 Dote Z4 n AC1-:\0NVLEDG01FN'T OF THE- P01 E-VI-IAL IMPACTS ON .A SI f-E PRO.I] APPLYING LAGOON' SLUDGE A� part (tit either u l iuoorl Opel'atlt}n Or 011-:10illU [Ilaill tell alice. the attached plan has been de% -eloped to apply ,lodge to Cite following, areas: Tracts &- Field 'Numbers: _ T=?y6? F- I_ "Ode using animal 11 age as a source of rltltrlems fir crops in lieu of inorganic tertlll/erg I, till ecMogically sound practice. pmducers should be aware that sludge that acculllulateb in a lagoon rna� haze concennations of nutrients and/or heml, metals. Accordingly, the quantity of phosphorus and micronutrle:lts in the Ilia€erial to be applied may exceed the fertilit\ requirements of planned emp;. Metals. Fli4gh ooncellkr{pions of metals in the sail can impact crap growth Or yields. The application of lagoon Mudge has the potential to significantly increase file concentration Of metals fparticulady copper and zinc) in the sail. \CSC and \C'DA&-CS recornmend that alternate sites for "We application be sought when soil concentrations of zinc (ZI1) exceed 142 Ts'ac (Znd of?{}00) or capper (C'ti) exceed 72 Is be (04 of 2019. A Cud or Zn-1 of ;{lT) is recognized as a critical toxic level tar same craps. For- peanuts. Sterna& e Kites are recommended when the Zn-1 iK 00. and a Zn-1 of 500 is recognized an a critical toxic level Producers shmdd be aware of the Pont -application Ctl and Zn concentl•ations predlcted on the sites planned for Wid4ue application. .adclitionalh.. soil pH should he maintained at (11) or above to minimize risk- of toxicirn-. Pl]osphortty Pho phorun (Pt eoncemradon in lagoon sludge may be high. Because P ads ,',rbs (into iron, aluminum. and Caliiulll. the soil Can bind and store excen P. \vh,n p concentrations reach higher concentration, We Is an increasing potential for P to be transported offsite and become a pollutant of surface waters. This transpoii rlla� occur thwugh soil erosion, or as a soluble form in Ktirfac:e rllr otf or leachin`''. An assessment of the Ask for P Wss to surface water h recltlimd as part of -a nutrient manactement plan for penWned operations or those rec& ing federal or state cost -share assistance. ] f the potential for P transport offsite is higlh. then future application ofaninml "uqe nm% not be allowed in a ntitl-ient management plan. Producers should be aware that apply ir14� lagoon slUdge May 1.inli€ the ability to use the site t'01- future animal "Ime application. Accordingly, appting lagoon Mudge to fields that are planned tcsr fLltLire Wa:te application as part of a nutrient manac.),ement plan is not advised. I ujider.;mnd that irppl ring maernnwrienB of 1r7lcr-(lrlrrtJ'to as a[ iwje.� that�7�11!/lcCrlllll' c.1.Ceed 117E c-lptcted crop removal could limit the -1r11mv tue Ol the f1C'IC1 m a 1, rite applic ltioll site. Cll!Cl r17 snore Cases, llcuativcl illlpaci /irtrn-c' phni armsih. I i•olimiarrli- agree to aphlt- slrgge to the fields idelili/ied above that 1 wvii or operate according to the atla,-hc d rlrrtrient m(magemcm plant or lauonlr C s7li-,p1ml. (Nod; larlcdoll-ner and /ar mer:'oper ator 1l im sigh-1 Liz (II her Date Fcrrrrrc�r,� Upc�rcrtclr-' I��{rf R C S. A �kv 244 (i'-Kml t c•b'Ifl- F;^�: ,;j - r.: (.\my 1 _. = t Or tl -- .-., , . 1 v in: i-- ACKNOWLEDGEMENT OF THE POTENTIAL IMPACTS ON A SITE FROM APPLYING LAGOON SLUDGE As part of either a lagoon closure operation or on -going lagoon maintenance. the attached plan has been developed to apply sludge to the following areas: Tracts & Field Numbers: 7--3A81 .. F-; y While using animal waste as a source of nutrients for crops in lieu of inorganic fertilizers is an ecologically sound practice. producers should be aware that sludge that accumulates in a lagoon may have high concentrations of nutrients and/or heavy metals. Accordingly, the quantity of phosphorus and micronutrients in the material to be applied may exceed the fertility requirements of planned crops. Metals. High concentrations of metals in the soil can impact crop gro�N'tlh or yields. The application of lagoon sludge has the potential to significantly increase the concentration of metals (particularly copper and zinc) in the soil. NICSU and NCDA&CS recommend that alternative sites for waste application be sought when soil concentrations of zinc (Zn) exceed 142 Ibs.:ac (Zn-I of 2000) or copper (Cu) exceed 72 lbs/ac (Cu-I of 2000). A Cu-I or Zn-I of 3000 is recognized as a critical toxic level for some crops. For peanuts. alternative sites are recommended when the Zn-I is 300, and a Z11-1 of 500 is recognized as a critical toxic level. Producers should be aware of the post -application Cu and Zn concentrations predicted on the sites planned for sludge application. Additionally, soil pH should be maintained at 6.0 or above to minimize risk of toxicity. Phosphorus. Phosphorus (P) concentration in lagoon sludge may be high. Because P adsorbs onto iron. aluminum. and calcium. the soil can bind and store excess P. When P concentrations reach higher concentrations, there is an increasing potential for P to be transported offsite and become a pollutant of surface waters. This transport may occur through soil erosion.. or as a soluble form in surface runoff or leaching. An assessment of the risk for P loss to surface Water is required as part of a nutrient management plan for permitted operations or those receiving federal or state cost -share assistance. If the potential for P transport offsite is high, then future application of animal waste may not be allowed in a nutrient management plan. Producers should be aware that applying lagoon sludge may limit the ability to use the site for future animal waste application. Accordingly, applying lagoon sludge to fields that are planned for fttture waste application as part of a nutrient management plan is not advised. 1 understand that applving ttiac'r011t11T'tC'1115 Or m ci-onutr eats al fates that signtflcantl}' exceed the evpected crop removal could limit the f am-e use of the field as a waste application site, and in some crises, negatirelr impact Titu re plant groirlli. 1 t'oluntai-ilr agree to apply sludge to the fields ideniified above that 1 own or operate according to the attached nudrient managertaent plant or lagoon closure plan. (*Both landowner and f v-mer'operaloi- must sign.) Ot1'trer' Date Fainter Operator* Date CN%MP De%elopment and lmplementativri Checkhr i \RCS. NC itt«� 2009 (Retired Feb 2017--Appmpnate tip Ct (NIP Case file DOcumentation. Feb 2017 Signature Page Required) P ' ACKNOtYLEDGEMENT OF THE POTENTIAL IMPACTS ON A SITE FROM APPLYING U100ON SLUDGE As part of either a lagoon closure operation or on -going lagoon maintenance, the -attached plan has been developed to apply sludge to the following areas: Tracts & Field Numbers: _ y While using animal waste as a source of nutrients for crops in lieu of inorganic Alizers is an ecologically sound practice, producers should be aware that sludge that accumulates in a lagoon may have high concentrations of nutrients and/or heavy metals. Accordingly, the quantity of phosphorus and micronutrients in the material to be applied may exceed the fertility requirements of planned crops. Metals_ High concentrations of metals in the sail can impact crop growth or yields. The application of lagoon sludge has the potential to significantly increase the concentration of metals (particularly copper and zinc) in the soil. NCSU and NCDA&CS rem mend that alternative sites for waste application be sought when soil concentrations of zinc (Zn) exceed 142 lbs/ac (Zn-1 of 2000) or copper (Cu) exceed 72 lbs/ac (Curl of 2000). A Cu-1 or Zn-1 of 3000 is recognized as a critical toxic level for some crops. For peanuts, alternative sites are recommended when the Za-1 is 300, and a Zn-I of 50D is recogrzed as a critical toxic level. Producers should be aware of the post -application Cu and Zn Concentrations predicted on the sites planned for sludge application. Additionally, soil PH should be maintained at 6 0 or above to minimize risk of toxicity. P torus. Phosphorus (A) concentration in lagoon sludge may be high. Because P adsorbs onto iron, aluminum, and calcium, the soil can bind and store excess P. When P concentrations reach higher concentrations, there is an increasing potential for P to be transported offsite and become a pollutant of surface waters. This transport may occur through soil erosion, or as a soluble form in surface runoff or leaching. An ant of the risk for P loss to surface water is required as part of nutrient nwaganrrtt plan for Permitted operations or those receiving federal or state cost -share assistance. If the potential for P transport offsite is high, then future application of animal wage may not be nilowed to a nutrient management plan. Producers should be aware that applying lagoon sludge may limit the abdity to use the site for future animal waste application, Accordingly, applying lagoon sludge to fields that are planned for future waste application as part of a nutrient managenerd plan is not advised. I understand that app6 ing nweronutrients or mkwnurrients at rates that significantly exceed the expected crap removal could hmit the future use of the field as a waste application site, and in sonte cases negatireb rnipact future plant growdt. I voluntarily agree to apply sludge to the fields ident f ed above that I ou-n or operate according to the attached nutrient management plan or lagoon closure plan. 'Both landowner and farmer/operator must sign, j 5� a�3 0o'ner" Date AMmtt or" Date CN*t? Dnckpaaa ana Impkrwntitice ChcedW NICS, NC Ms t ?M I Roared F ib 2017-Ap4 mpm"c For CNNiP Cam Fie Daawwmt6m F eb 7017 Sa lrc Zc R CifiAir ed� ACKNOWLEDGEMENT OV7118 MTrr41J*L .11WPACg7S Oro A Sf E FROM APPLYING P AGCO4 SLUnGE As pan of either a lagoon closure operattoh or ongoing lagoons maintenance, the srracl plan has been developed to apply sludge to the following areas; Tracts & Fidd Numbcrr T— S . '�1 While using animal waste as a solace of nutrients for crops in lIV" of st�ic fem'1zerg is an ecologically sound practice, producers should be srvwe that sludge that saccunulatcs in a lagoon inay have high concentrations of nutrients and/or heavy metals. Accordingly, the quantity of phosphorus and raicranutrients in the material to be applied may exceed the fatility requirements of planned crops. Metals. High concentrations of metals in the soil can impact crop growth or yield application of lagoon sludge has the potential to significamly irmnum the tarcertiratibn of metals (Particularly copper and zinc) in the soil. NCSU and NCDA&CS recommend that ahemative sites for waste application be sought when soil concaitmtiow of tine (Zn) exceed 142 RWac (Zn-1 of 20W) or copper (Cu) exceed 72 ]bslac (CO-] bf2000). A Cu-1 or Zn-1 of 3000 is recognized as a critical toxic level for some crops. For pearmta, alternative sites are recommended when the Zn-1 is 300, and a Zn-1 of 5W is recbgmz+ed as a critical toxic level. Producers should be aware of fire post -application Cu aril Zn concentrations predicted on the sites planned for sludge application. Additionally, soil pH should be maintained at 6.0 or above to minimize risk oftoxicity. P rus- Phosphorus (P) concentration in lagoon sWV may be high. Buse P adsorbs onto iron, aluminum, and calcium, the soil can bind and store excess P. When P concentrations reach higher concentrations, there is an increasing potential for p to be transported oii'she and become a pollutant of surface waters. This tuauport may near through soil erosion, or as a soluble form in surface nmoffor leaching. An assessment of the risk for P loss to surface water is required as part of a nutrient managemmt pin for permitted operations or those receiving federal or state cost -share assistance, if the potential for P transport offsite is high, then fuhm applications of animal wane may rust be allowed in a nutrient management plan. Piodis = should be swam that applying lagoon sludge may limit the abi-lity to use the site for future adnnd waste application. Accordingly, applying Ngoon shrdge to fields that are planned for futm waste applications as part of a nutriem nmagetnent plan is not advised. 1 understand that applying macromrtrienis or miawminems at rates that signifimndy exceed the expected crop remoml could limit thefreture use of thefield as a note aMkamm site, and in some cases. negatively impaQct future plant Vvwh. I voluhtanly agree to apply sludge to the fields identified above that I own or operate according to the attached nv iemt managemew plan or lagoon closure plan. (+Both landowner and farmerloperator must sigm) Date Dlate CLAMP De►riopm-W wd !M*m=a,,, Cyst 4Ri S. NC N54y 2009 IXV traf Feb 2017—ApPmpnate btu C-NMP Case File DWWWOMl 6M. Feb 2017 Signamre Page Rcx}vp�d) P. 7 t._. .. .. _ �. , J -i" _, - IL I' .'. ' � ..` �i� t. r'S_ ..�5 v w '��! !1-,+,1;�• �.� M1 �' x ' �-'IC' P- J_-. ,M "'yt'Y t, .',�-' . `r_•;!L'..} 'I-:� 4� Y .i � y.,,, � -" ,".�5� ,,=",4'.,�4� .,'.e ... ..- _ }�til � '� ''t. .�t'i. I. ['!.:t �.. ": i �I..-`.'1 �k- °i'• k =r" �, ACKNOWLEDGEME:NT OF THE, P(ATNTIA1, CNIUACT� ON E FROM APPI VIINC, I 1(,()ON 51 t'r)(7,F lux K"m W= 10ye lo the Nab %x mv wea- Tmms 'mile uVro WK? 1: wo �.V:jjn 7"r on!, 0AqUyQQ AM Me jap im? =M"AT25 r, 0 _CI C 4 21rL ML - % L co;n er�o MV p A " p p ne "Onc t loci 42 its mnzV J2445 '7 %Cr7r)',:7 1, L yZV Zp,: 0,V yj ot fL MMrnoe Nn "Yny, Xo.p TOZZ but Q n4 U A�ry 5 Inv KNOW Z O�: V�nj �f OnAn 1 Oro, a F: V N 7C 10 F.- 7:7: p LZ moon son :10 110 at 7= jbM-_. L.LZI. z upon *-Ago I i k I-- L , rf r Date- 11; 21 e2022 WASTE UTILIZATION MAP it(s) SWIFT CREEK HOG FARM Field Ofkv NASHVILLE SERVICE CENTER cnct- NASH SOIL & WATER CONSERVATION DISTRICT Agency: NRCS Assisted By John Long State and County: Nash County, North Carolina Prepared with assistance from USDA -Natural Resources Conservation Sery oe TRACTNBR 6870 Property_Line_Buffer 25_Ft j Ditch_Buffer_25_Ft Streams Roads 0 330 660 1,320 1,980 Feet Date: 11 /21/2022 WASTE UTILIZATION MAP ;i SWIFT CREEK HOG FARM Field Offce NASHVIt LE SERVICE CENTER ANASH SOIL & WATER CONSERVAT ON DISTRICT Agency. NRCS Assisted By John Long State and County Nash County, North Carolina Legal Description Tract 4622 4622 Pro perty_Line_Buffer_25_Ft Ditch_Buffer4 } Well ® Wel1_Buffer_100_Ft Roads Prepared with assistance from USDA -Natural Resources UonservaPMr, Service 0 330 660 1,320 1,980 MMOM Feet Date. 0302;2023 WASTE UTILIZATION MAP SWIFT CREEK HOG FARM Fie;d Otfi^e NASHVILLE SERVICE CENTER Agency N �t: NASH SOIL & WATER CONSERVATION DISTR-CT Assisted By: y: John Long State and County Nash Counly, North Carolina Legal Description: Tract 3669 3669 D 330 660 1,320 1,980 Property_Line .Buffer_25_Ft Feet ,j Ditch Buffer 25_Ft ® Well_Buffer_.100 Yt Streams Roads Dale: OM212023 WASTE UTILIZATION MAP sI SWIFT CREEK HOG FARM Field Office, NASHVILLE SERVICE CENTER -1. NASH S01L & WATER CON SERVAT[ON DISTRICT Agency: NRCS Msis#ed By' John Long Slate and County; Nash County, Norm Carolina Lega' Descrip."n: Traci 3719 3719 0 330 660 1,320 1,980 Property_t_ine_Buffer_25_Ft _i Ditch_ Buffer _25_Ft ® Well_Buffer__l00_Ft Streams Feet Roads Date: 03/02/2023 WASTE UTILIZATION MAP s} SWIFT CREEK HOG FARM F eld Office NASHVILLE SERVICE CENTER .,;t NASH SOIL & WATER CONSERVATION D'STRICT Agency, NRCS Assisted By. John Long State and County: Nash County. Notch Carolina Legal Descrpt on: Tract 3703 3703 Pro perty_Line_Buffer_25_Ft L I DitchBuffer25_Ft LA Well —Buffer 100_Ft Streams Roads Prepared with assistance from USDA -Natural Resources Conservation Service 0 330 660 1,320 1,980 Feet Date: 03/0212023 WASTE UTILIZATION MAP s) SWIFT CREEK HOG FARM Field Office NASHVILLE SERVICE CENTER ct. NASH SOIL & WATER CONSERVATION DISTRICT Agency NRCS Assisted By: John Long State and County Nash County, North Carolina Legal Description. Tract 3645 Prepared with assistance from USDA -Natural Resources Conservation Service 3645 0 330 660 1,320 1,980 Property_Line_Buffer_25_Ft 1111IMNEI Feet i Ditch_ Buffer _25_Ft ® Well_Buffer_100_Ft Streams - Roads Date: 09AW022 WASTE UTILIZATION MAP r S) SWIFT CREEK HOG FARM Fiehd Office. NASH ILLE SERVICE CENTER NASH SOIL & WATER CONSERVATION DISTRICT Agency_ NRCS Assisted 13y: John Long Slate and County_ Nash County, N DM Carohria Legend Prepared with assistance trom UbUA-Natural Kesources conservation aervice TF TNBR M Ditch —Buffer 25_Ft 3670 Pro perty_Lines_Buffer_25_Ft # Well ® Non_Farrrl_Residence_Buffer_200_F4 Streams Well —Buffer, 100_Ft Roads ® Surface WaterBuffer 0 330 660 1,320 1,980 Feet Date: 09/09/2022 WASTE UTILIZATION MAP t(s) SW -FT CREEK HOG FARM Field Office NASHVILLE SERVICE CENTER irict. NASH SOIL 8, WATER CONSERVATION DISTRICT Agency. NRCS Assisted By John Long State and County Nash County, North Carol.^a Legal Description. Tract 4733 Legend Prepared with assistance from USDA -Natural Resources Conservat on Service TRACTNBR ® Ditch_Buffer_25_Ft 4733 Pro perty_Lines_Buffer_25_Ft Well ® Non Farm Residence_ Buffer _200_Ft ® Well_Buffer_100_Ft Roads Streams lossooff- MOM 0 330 660 1320 1,980 Feet Date: 0910912022 WASTE UTILIZATION MAP it(s}-SWIFT CREEK HOG FARM Fieid Office NASHVILLE SERVICE CENTER 'tr ct NASH SOIL & WATER CONSERVATION DISTRICT A9er�cy. NRCS Assisted By: John Long State and County Nash County North Carolina Lega Descr pt on: Tract 3741 Legend Prepared with assistance from USDA-Natura` Resources Conservat-on SerV CH TRACTNBR M Ditch— Buffer_25_Ft 3741 Pro perty_Lines_Buffer_25_Ft Well ® Non —Farm Reside nce_Buffer_200_Ft ® Well_Buffer_100_Ft Roads - Streams 0 330 660 1,320 1,980 Feet