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HomeMy WebLinkAboutwq0006906_Regional Office Historical File Pre 2018 (2)State of North Carolina Department of Environment, Health and Natural Resources Division of Water Quality James B. Hunt, Jr., Governor Jonathan B. Howes, Secretary A. Preston Howard, Jr., P.E., Director N.C. DEPT. OF October 7, 1996 RNVIRortDA.,NT, H .SUM, fn NATURAL RESOURCtS Mr. David M. Robinette, Public Works Director Town of Taylorsville OCT 0 1996 204 Main Avenue Drive, SE Taylorsville, North Carolina 28681 OlVISl011 OF tilHA&E3IE11T Subject: Permit No. WQ0006906M'ONESULE 1010IIAL OFFICE Town of Taylorsville Land Application of Wastewater Residuals Alexander County Dear Mr. Robinette: In accordance with your application received on August 26, 1996, we are forwarding herewith Permit No. WQ0006906 dated October 7, 1996, to the Town of Taylorsville for the operation of a wastewater residuals land application program. This permit is to add two new land application sites, the Robert Lynn Marshall Site and the Donald G. Payne Site. Please note, the Herman Dairy Farm, Inc. Sites AL 2-1 through AL 2-4 have been withdrawn from this permit in compliance with the wishes of the property owner. This permit shall be effective from the date of issuance until October 31, 1997, shall void Permit No. WQ0006906 issued November 13, 1992, and shall be subject to the conditions and limitations as specified therein. Please pay particular attention to the monitoring and reporting requirements contained in this permit. Failure to establish an adequate system for collecting and maintaining the required operational information will result in future compliance problems. If any parts, requirements, or limitations contained in this permit are unacceptable, you have the right to request an adjudicatory hearing upon written request within thirty (30) days following receipt of this permit. This request must be in the form of a written petition, conforming to Chapter 150B of North Carolina General Statutes, and filed with the Office of Administrative Hearings, P.O. Drawer 27447, Raleigh, NC 27611-7447. Unless such demands are made this permit shall be final and binding. If you need additional information concerning this matter, please contact Mr. John Seymour at (919) 733-5083 extension 546. Sincerely, r r4re ston ward, Jr., P.E. cc: Alexander County Health Department Mooresville Regional Office, Water Quality Section •Mooresville Regional- Office -Groundwater Section Bob Cheek, Groundwater Section, Central Office Training and Certification Unit Facilities Assessment Unit P.O. Box 29535, Raleigh, North Carolina 27626-0535 Telephone (919) 733-5083 FAX (919) 733-0719 An Equal Opportunity Affirmative Action Employer 50% recycled/ 10% post -consumer paper 6. All residuals included in this permit must be monitored annually from the date of permit issuance, for compliance with condition I.11 of this permit. Data to verify stabilization and vector attraction reduction of the residuals must be maintained by the Permittee. The required data is specific to the stabilization process utilized, but should be sufficient to clearly demonstrate compliance the Class A pathogen requirements in 40 CFR Part 503.32(a) or with the Class B pathogen requirements and site restrictions in 40 CFR Part 503.32(b), and one of vector attraction reduction requirements in 40 CFR Part 503.33. In addition, the EPA certification statements concerning compliance with pathogen requirements, vector attraction reduction requirements and management practices must be completed annually by the proper authority or authorities if more than one is involved, either the person who prepares the residuals, the person who derives the material, or the person who applies the residuals. 7. Three copies of all required monitoring and reporting requirements as specified in conditions III 1, III 2, III 3, III 4, III 5 and III 6 shall be submitted annually on or before March 1 of the following year to the following address: NC Division of Water Quality Water Quality Section Facility Assessment Unit PO Box 29535 Raleigh, NC 27626-0535 8. Noncompliance Notification: The Permittee shall report by telephone to the Mooresville Regional Office, telephone number 704/ 663-1699 as soon as possible, but in no case more than 24 hours or on the next working day following the occurrence or first knowledge of the occurrence of any of the following: a. Any occurrence with the land application program which results in the land application of significant amounts of wastes which are abnormal in quantity or characteristic. b . Any failure of the land application program resulting in a release of material to receiving waters. Any time that self -monitoring information indicates that the facility has gone out of compliance with the conditions and limitations of this permit or the parameters'on which the system was designed. d: Any process unit failure, due to known or unknown reasons, that render the facility incapable of adequate residual treatment. e. Any spillage or discharge from a vehicle or piping system transporting residuals to the application site. Persons reporting such occurrences by telephone shall also file a written report in letter form within five (5) days following first knowledge of the occurrence. This report must outline the actions taken or proposed to be taken to ensure that the problem does not recur. I V . GROUNDWATER REQUIREMENTS For areas that are prone to flooding or within the 100-year flood elevation, residuals may be applied only during periods of dry weather (April through November). The residuals must be incorporated into the soil within twenty-four (24) hours of application. 7 2. The COMPLIANCE BOUNDARY for the disposal system is specified by regulations in 15A NCAC 2L, Groundwater Classifications and Standards. The Compliance Boundary is for the disposal system constructed after December 31, 1983 is established at either (1) 250 feet from the waste disposal area, or (2) 50 feet within the property boundary, whichever is closest to the waste disposal area. An exceedance of Groundwater Quality Standards at or beyond the Compliance Boundary is subject to immediate remediation action in addition to the penalty provisions applicable under General Statute 143-215.6A(a)(1). In accordance with 15A NCAC 2L, a REVIEW BOUNDARY is established around the disposal systems midway between the Compliance Boundary and the perimeter of the waste disposal area. Any exceedance of standards at the Review Boundary shall require remediation action on the part of the permittee. 3. Any groundwater quality monitoring, as deemed necessary by the Division, shall be provided. 4. No land application of waste activities shall be undertaken when the seasonal high water table is less than three feet below land surface. V . INSPECTIONS 1. The Permittee or his designee shall inspect the residuals storage, transport, and application facilities to prevent malfunctions and deterioration, operator errors and discharges which may cause or lead to the release of wastes to the environment, a threat to human health, or a nuisance. The Permittee shall maintain an inspection log or summary including at least the date and time of inspection, observations made, and any maintenance, repairs, or corrective actions taken by the Permittee. This log of inspections shall be maintained by the Permittee for a period of five years from the date of the inspection and shall be made available to the Division of Water Quality or other permitting authority, upon request. 2. Any duly authorized officer, employee, or representative of the Division of Water Quality may, upon presentation of credentials, enter and inspect any property, premises or place on or related to the application site or facility at any reasonable time for the purpose of determining compliance with this permit; may inspect or copy any records that must be kept under the terms and conditions of this permit; and may obtain samples of groundwater, surface water, or leachate. VI. GENERAL CONDITIONS This permit shall become voidable unless the land application activities are carried out in accordance with the conditions of this permit, the supporting materials, and in the manner approved by this Division. 2. This permit is effective only with respect to the nature and volume of wastes described in the application and other supporting data. 3. This permit is not automatically transferable. In the event that there is a desire for the facilities to change ownership or a name change of the Permittee, a formal permit request must be submitted to the Division of Water Quality accompanied by an application fee, documentation from the parties involved, and other supporting materials as may be appropriate. The approval of this request will be considered on its merits and may or may not be approved. �3 4. The following are approved sites for residuals application (see attached map(s)): Application Area [acres] Site No. Owner/Lessee (excluding buffers) AL 3-1 Bill Pope 11.0 AL 4-1 Robert L. Marshall 23.1 AL 4-2 Robert L. Marshall 15.5 AL 4-3 Robert L. and William H. Marshall 11.4 AL 5-1 Donald G. Payne 10.3 AL 5-2 Donald G. Payne 11.8 AL 5-3 Donald G. Payne 12.9 AL 5-4 Donald G. Payne 12.8 AL 5-5 Donald G. Payne 12.5 AL 5-6 Donald G. Payne 12.1 AL 5-7 Donald G. Payne 12.1 AL 5-8 Donald G. Payne 6.0 AL 5-9 Donald G. Payne 73.0 AL 5-10 Donald G. Payne 7.4 AL 5-11 Donald G. Payne 6.0 AL 5-12 Donald G. Payne 5.2 AL 5-13 Donald G. Payne 4.5 AL 5-14 Donald G. Payne 3.4 AL 5-15 Donald G. Payne 7.8 AL 5-16 Donald G. Payne 11.4 AL 5-17 Donald G. Payne 8.3 TOTAL AVAILABLE ACRES 278.5 5. Failure to abide by the conditions and limitations contained in this permit may subject the Permittee to an enforcement action by the Division of Water Quality in accordance with North Carolina General Statute 143-215.6(a) to 143-215.6(c). 6. The annual administering and compliance fee must be paid by the Permittee within thirty (30) days after being billed by the Division. Failure to pay the fee accordingly may cause the Division to initiate action to revoke this permit as specified by 15 NCAC 2H .0205 (c)(4). 7. The issuance of this permit does not preclude the Permittee from complying with any and all statutes, rules, regulations, or ordinances which may be imposed by other government agencies (local, state, and federal) which have jurisdiction. 8. The Permittee, at least six (6) months prior to the expiration of this permit, shall request its extension. Upon receipt of the request, the Commission will review the adequacy of the facilities described therein, and if warranted, will extend the permit for such period of time and under such conditions and limitations as it may deem appropriate. 9. This permit may be modified, or revoked and reissued to incorporate any conditions, limitations and monitoring'requirements the Division of Water Quality deems necessary in order to adequately protect the environment and public health. E 10. This permit shall become voidable unless the agreements between the Permittee and the landowners/lessees are in full force and effect. The land owner agreements are considered expired concurrent with the expiration date of the permit and must be renewed at the same time the permit is renewed. Permit issued this the 7th day of October, 1996 NORTH CAROLINA ENVIRONMENTAL MANAGEMENT COMMISSION A. Preston ard, Jr., P.E., Director Division of Water Quality By Authority of the Environmental Management Commission Permit Number WQ0006906 10 Specializing in Land Application • Sludge Disposal VICINITY MAP N ylrlheelabmtor Clean Water Systems Inc. B&R0DivWo SuDlhcin krgum 908 Belnccr Dntr I`CIIInn1, Al. 3512-1 205.664.B440 205.664.767h 1:u L CH. RD ,Or�i 0 z p ° PLEASANT H ^ x im J 7. R AID n ' ► f O r = 7y z OLD 4Sh � RO s ,`IlG < OFF LOUDERMEL t9 GLPSS p t310 1 1KE ACTr ��F L� m ROCKY P'AC- J R'L O 9 v> .p Q R,P BnPH C)�` M T N ms W 3 g RO CH 1795' G y P C E O a.L+771) .I°(L CeMETEPy pO ROUNDTORol} 2 , y m � z Se o 1 A MTN \ 4, 0\ fF. N qp 146, 9 " i Y4E� o cos ?P pRF ¢ RAM1 SSLEJAI Y C 0 GpPs LIN ADAA,S� m jp1{NNY W/ ? 1416J (t41T) m a� o N U r 9� OTE MOOSE RD` -� 7rr t ° LE0000 9 Q fD l I1 E L o N--�'�— OX Py OURKE e `\ 1j414) FA' RD RD MgHSH �y* �O. t13 o v \9 (14y�l RD m9avil C ` CARSON CNAP� RD ° tm �^ OqK IN 1,31q Y ORSVILLE - '��i�-�? -S�'0 _' MUD19 foRK .A OTHER S1 I ROCKY SPRINGS q0 \'Pf',T SY LN y LN O COME A4ccL EL \ W h faf U 5 O \H5 (149T1 i11, S �` 90 64 Q P _ G < J = Q\. W w OBLE RD ^ `�'AfF,�'gN p F yS 5 VER j O f 1 i _�61f9 RR _w n ' Slalt ➢ ��,^3� �nyy �.n Cep 90 SOS" t-- < _ Daa ^ Z) yt`' O OOP O 0. ` CHA ANC ?p CAA 1i ¢ no > p` ( J �)" awn ••,.u� A J RI Suit ti Ap ' 6 3 y lDRF„ UN- ? �P` 1,`� CH W=( O tit]1 IDDENITE- A J ¢ }\Q'� MACED ONIP W 90 ..J 2 . i p Aq T,N TTT r0 w i --IkD OUNO,. L1605) i.y1LL YY ^p` t -A 17�(/` °'4T U 0 V'r l O 1T� `► it 27) tIT (Q J FAIR V)ay C Rp L pFI Ge TTI 9 \^6 ]11 �C 0 CLN RD 02 CT OWO0O s PO J LIBERTY CN"RO O' L%O AIPSp,,, LN N\` Cl ° HFNRy �? D O o ry ALLENDALE \ '.,°� yO°o• WKELPIN LN IT. J.,YEi (1T�1 1-42) S a 90 SE H001 PAXX 0 C ALSPr ° �, 1610 hi° 3 I.r� RD P ^ a LE SCALE: 1" = 2 miles Site AL4 A WHI.ELABR rok TECIINULWIEIS COMPANY VICINITY MAP Land Apphcaliun • 1)10•FIX AI6ulinc Slahihzanun IPS Cumpos(ing • Uryiug : nd l`dlc(ILing N PKIN"ITI) (IN KLf'11'I t I11'NIT11 A& 101,eelablator Clean !,Water systems Mc MtGRQD,,i' I U]"U'URAPHIC MAP Somhern Region 908 BcIchcr Drive Pelham. Al- 35124 2(0)5.664 . 8440 205.664.7679 Fax I \wu i I \1,pN1,ip I,, P-Ili, ­.w.v;N IT'S Ul-lmr—linp Urving a ... I PcIl'!uilip PRI111:1) ON Ry:r-yct.r.ri AL Wheelabratoi Clea» Water Systems In 908 Belcher I h I%r Pclll;uu, Al. 351 _2 1 205.66A.b440 205.60A.7676 Fax SCALE: 11t = 2 miles VICINITY MAP �.Jlld Al)hIICaI11L1 • 1310' I'I X Aliafii1C Stabilization A WHEELABRATOR TECHNOLOGIES IOMPAN'1 IPS C'ornlw�sung • Drying and Pellclizing Site AL5 N PRIN I LD ON RllA II II VAPte 0 107eelabrator Clean Water Systems Inc. Ir Southern Region 908 Belcher Drive Pelham. AL 35124 205.664.6440 • 201.664.7678 Fax SCALE: 1:24,000 Site AL5, Fields 1 through 17 TOPOGRAPHIC AIAP Land Application • R10- FIX Alkaline Stahilization N IPSCilml—ling • Dryingand Pellelizing PRINTED ON RECYCLED PAPER r r DIVISION OF WATER QUALITY GROUNDWATER SECTION s ep-r. 10, 17S� M E M O R A N D U M TO: �a 2 g� /1 .o G� r2-TIIAiv Regional Of f ice FROM:ti SUBJECT: Application for / Permit Renewal I. Pegrm�t- Arnendme t I� 'e'er 5e � New/ Permit Facility Name: %Jw�- �� lU'�S✓�G1 County: Type of Project: IAA�d. /{ �0�, Sl1"cle APPLICABLE PERMIT NO . s : WQ o oo G 70 6 U,GW 7.' UIC h]mCI EPA A to C CUA The Groundwater Section has received a copy of the referenced permit application, a copy of which should have been sent to your Regional Water Quality Supervisor - IF A COPY HAS NOT BEEN RECEIVED IN THE REGIONAL OFFICE, PLEASE LET ME KNOW. The Groundwater Section has received a copy of the referenced permit application. A p,X gf thZap-Uccat,i documents we ece ved is attaach�ed . The Groundwater Section has received a subsurface disposal project from the Div. Env. Health's On -Site Wastewater Section. A copy of the application has been forwarded to DEH's Regional Soil Specialist, Please coordinate your review with that Soil Specialist. _,-,Pleas_e-review the application materials for completeness. If you feel add"tional information is necessary, please let me know no later than A copy of any formal request for additional information .will be forwarded to you. If -you -do not need any additiona-l_=iifformatdi©n, to complete your review, please provide your final comments by ac.7• / t%9� .f you Copt MO= EmosNG aM3 UMnab AMTozamtUono \TRANS.SHL rl Wov GROUNDWATER SECTION GW # 176 DIVISION OF ENVIRONMENTAL MANAGEMENT RECORD OF WASTE DISPOSAL PERMIT APPLICATION REVIEW REVIEW BY C14yele DATE 9'n `916 FIELD INVESTIGATION? (Y/N) YPS FACILITY NAME ✓_own j '%&.y/osv ACE COUNTY LOCATION 76 r sv://PWC TYPE OF DISPOSAL SYSTEM (LAGOON, ETC.) S�v� �' �4 ''a" DESIGN CAP. (GPD) Wo DESCRIPTION OF FACILITY ) Mof s4v/1 /7 �kAvFd.—1 01 SIZE OF IMPOUNDMENT (FT. SQ.) &/OR SIZE OF APPLICATION AREA 2 9 -?• S `e'FS WASTE SOURCE: MUN. SLUDGE MUN. W. WATER: PRIMARY SECONDARY TERTIARY IND. SLUDGE IND. WELL WATER OTHERS: DISTANCE FROM WASTE SOURCE TO NEAREST: STREAM FOR WELL: TYPE OF USE St�� , DEPTH WHA/T1 DESIGN CONDITIQNS WILL REDUCE/IN REASYHA r,,.�� F s ✓� > WO FT., WELL y rov FT. ����%Ja/ I& ` Ile" 6. & sQi%"fe/6 PUMP RATE (EST.) ? OF �GW CONTAMM NATION: Ilah eel- ! f- &'l ��Prs WHAT NATURAL SITE CONDITIONS WILL REDUCE/INCREASE CHANCE OF GW CONTAM ATION: dPffk!af 5011/5 . l&'-a c./ 4,,en 916,c&5 , /­ /z' a./ Dafr'ans cv. /l l --cos .�a�� rc '<-a ti . DEPTH TO: BEDROCK ? y FT., SEASONAL HIGH W.T. FT., ANNUAL W.T. FLUX } FT. SURFICIAL AQUIFER GEN. LITHO .OGY �y Z.— � t/.y 4 41'� HYD. COND. '� �� +z FT./DAY ❑MEASURED [,t ESTIMATED THICKNESS FT. NO. OF MONITER WELLS: PROPOSED: UP 0 FROM WORKSHEET: SITE NUMERICAL DESCRIPTION= BEDROCK/(ARTESIANAQUIFER / Grb�,•�� � (06sC✓J�(' T"l(94( M <<(Cil ❑ MEASURED FT./DAY ® ESTIMATED DOWN 0 ; EXISTING: UP DOWN c2 T 1 2 3 4 5 6 6A 613 SITE GRADE (HYDROGEOL.) = PROPOSED SAMPLING SCHEDULE & PARAMETER(S): SITUATION GRADE= HAVE THERE BEEN ANY EXCEEDANCES OF THE GROUNDWATER STANDARDS? YES NO HAS ANY ENFORCEMENT ACTION BEEN TAKEN? YES NO DATE OF ACTION: BRIEF SUMMARY OF ENFORCEMENT ACTION TAKEN: REMARKS/ RECOMMENDATIONS (Continue on reverse, if necessary): 6e �q/ �,�' lee) Ll'le 401/40 .41-5v%te a ell •'�/�S Az s -� /6 4,pr GW-48 Revised 04/94 HYD. REGIONAL UPERVISOR DIVISION OF ENVIRONMENTAL MANAGEMENT GROUNDWATER SECTION September 30, 1996 MEMORANDUM To: Carolyn McCaskill Through: Bob Cheek From: Brian Wootton Subject: Town of Taylorsville Amendment to Permit No. WQ0006906 Land Application of Sludge Alexander County WQ0006906/GW96176 (John Seymour: DEM SERG Review Engineer) N.C. Dti >T. O_F HNVIRONp,IFNT, HEALTH, NATUR 6,L OCT l r� RIM?] OFIT The Groundwater Section has reviewed the subject permit amendment request for an additional 267.5 acres to the sludge land application program. We have no objection to issuance of the permit, provided that the following conditions are included: 1. No land application of waste activities shall be undertaken when the seasonal high water table is less than three feet below land surface. 2. For areas that are prone to flooding or within the 100-year flood elevation, residuals may be applied only during periods of dry weather (April through November). The residuals must be incorporated into the soil within twenty-four (24) hours of application. 3. The COMPLIANCE BOUNDARY for the disposal system is specified by regulations in 15A NCAC 2L, Groundwater Classifications and Standards. The Compliance Boundary for the disposal system constructed after December 31, 1983 is established at either (1) 250 feet from the waste disposal area, or (2) 50 feet within the property boundary, whichever is closest to the waste disposal area. An exceedance of Groundwater Quality Standards at or beyond the Compliance Boundary is subject to immediate remediation action in addition to the penalty provisions applicable under —I 1• V � r 41 State of North - arolina j Department of Environment, l r Health and Natural Resources Division of Water Quality b �•r 7 James B. Hunt, Jr., Governor Jonathan B. Howes, Secretary A. Preston Howard, Jr., P.E., Director >°FALTx, �s NATURAL RESOURCES SEP 6 1996 August 27, 1996 MR. ROBERT W. DUNCAN olalslM. R Er+ LE REGINIAL OFFlCEE1i1ENT MOORESV�.LE AEOIOrIAL OFFICE TUW1V uF iAY`iGRjViLLE 204 JAI^ ..^_VR P. P'IVE SE TAYLORSVILLE, NORTH CAROLINA 28681 Subject: Application No. WQ0006906 A Sludge Facility Sludge -Land Application Alexander County Dear MR. DUNCAN: The Division's Permits and Engineering Unit acknowledges receipt of your permit application an6 supporting materials on August 26, 1996. This application has been assigned the number listed above. Your project has been assigned to John Seymour for a detailed engineering review. Should there be any questions concerning your project, the reviewer will contact you with a request for additional information. Be aware that the Division's regional office, copied below, must provide recommendations from the Regional Supervisor or a Procedure Four Evaluation for this project, prior to final action by the Division. If you have any questions, please contact John Seymour at (919) 733-5083 extension 546. If the engineer is unavailable, you may leave a message on their voice mail and they will respond promptly. PLEASE REFER TO THE ABOVE APPLICATION NUMBER WHEN MAIKING INQUIRIES ON THIS PROJECT. cc 1Moo>esvi`IleZZegzoriaf-Office Bio Gro Sincerely, YarolMyn7MMcCaskill Supervisor, State Engineering Review Group Pollution Prevention Pans P.O. Box 29535, Raleigh, North Carolina 27626-0535 Telephone 919-733-7015 An Equal Opportunity Affirmative Action Employer Town of Taylorsville Land Application Sites .......... ....................... . . .............. .... N.C. DF-FT- 13F F,j,,TV1RONM5-T-1T, REAL"", & NATURAL r'H'SOLJRGEB SEP 6 1996 gIVIS12,11 OF ClivipGIRMITAL MAMMIMIT - - mmlm-Ll �1410A- ff—HE Town of Taylorsville Land Application Sites August 20, 1996 m;mxm ........ .... . ....... ... .. .... ................. ... . . ... .... .... Wheelabrator Water Technologies Inc. Bio Gro Division Wheelsbrator Water Technologies Inc. Rio Oro Division A WMX Technologies Company Tel. 205.664.8440 Southern Region Fax 205.664.7678 908 Belcher Drive Pelham, AL 35124 August 21, 1996 Mr. Donald Safrit Division of Water Quality 512 North Salisbury Street Raleigh, NC 27604 Re: Land Application Sites Town of Tayiorsville Dear Mr. Safrit: Please find attached for your consideration site specific information on the following land application sites located in Alexander County. Robert Lynn Marshall Site AL4, Fields 1 through 3 Donald G. Payne Site AL5, Fields 1 through 17 If you have any questions or require additional information, please contact me at 704.732.8500 or John Scaduto at 205.664.8440. Sincerely, Robert Hamilton Technical Specialist O To: Permits and Engineering Unit PRIORITY: YES Water Quality Section (see Part IV) Atten: John Seynmour Date: September 13; 1996 NON -DISCHARGE STAFF REPORT AND RECOMMENDATION County: Alexander Permit No.: WQ0006906 MRO No.: 96-171 PART I - GENERAL INFORMATION 1. Facility and Address: Town of Taylorsville Sludge Land Application .204 Main Avenue Drive, SE Taylorsville, North Carolina 28681 2. Date of Investigation: September 12, 1996 3. Report Prepared By: Michael L. Parker, Environ. Engineer rI 4. Persons Contacted and Telephone number: Robert Hamilton, Bio-Gro, (704) 732-8500. 5. Directions to Site: See permit application for locations of the various sludge land application sites. 6. Disposal Site(s), List for all disposal sites: See permit application for coordinates of sludge land application disposal sites. Attach a USGS Map Extract and indicate sludge disposal_ site(s) on map. (See permit modification request) 7. Size: The Town has submitted ti 268 acres for inclusion into their land appliaction program. 8. Topography: Neither of the two sites are located within the 100 year flood plain. Portions of both sites which have slopes >10% will be buffered for surface application. 9. Location of Nearest Dwelling and Water Supply Well: There are both wells and residences located adjacent to both land application sites, however, all appear to be properly buffered in the application package. 10. Watershed Stream Basin Information: See permit application for Watershed information a. Watershed Classification: Fields AL4 1,2,3: C Fields AL5 1-17: WS-II b. River Basin and Subbasin No.: Catawba; 030832 C. Distance to surface water from disposal System: Varies depending on the site (see Permit application). Page Two PART II - DESCRIPTION OF DISCHARGE AND TREATMENT WORKS 1. Type of sludge: 80% Domestic* 20% Industrial_* t Estimate The Town has one significant industry and is in the process of developing a pretreatment program. a. Volume: 85 Dry tons per year (estimated) b. Types and quantities of industrial wastewater: The primary industrial contributor is a textile stone washing operation. C. Prevalent toxic constituents in wastewater: none that we are aware. d. Pretreatment Program (POTWs only): The Town of Taylorsville does not have a Pretreatment Program. 2. Current Permitted Capacity: N/A 3. Type of Treatment: Existing sludge treatment consists of aerobic digestion. The sludge drying beds are no longer used. 4. Sludge Handling and Disposal Scheme: In the past, sludge was taken to the municipal landfill. The Town plans to rely on land application for all future disposal needs. 5. Treatment Plant Classification: Class III 7. SIC Code(s): 4952 Wastewater Code(s): 01 Main Treatment Unit Code: 40003 PART III - OTHER PERTINENT INFORMATION 1. Is this facility being constructed with Construction Grant Funds (municipals only)? N/A 2. Special monitoring requests: N/A 3. Air Quality and/or Groundwater concerns or hazardous materials utilized at this facility that may impact water quality, air quality, or groundwater? Groundwater comments should be obtained. There are no known Air Quality or hazardous materials concerns. i 6 Page Three PART IV - EVALUATION AND RECOMMENDATIONS The applicant, Town of Taylorsville, has applied for a modification of its non -discharge permit for the addition of ti 268 acres to its sludge land application program. Comments on the proposed land application sites are as follows: Fields AL4-1,2,3 Slope (topography) will restrict a portion of the available area. These areas have been buffered by the applicant. Excellent soil depth and cover crop Were found during the site investigation. These fields are well buffered on the north, west, and south sides. Fields AL5 1-17 Fields 1-15 are actually strip crop rows, which are contiguous with each other. The fields were segregated by the land application contractor for operational purposes. All of the fields (1-17) have established cover crops and deep, well drained soils. Appropriate buffering will be necessary for those areas adjacent to water courses, dwellings, and property lines. It is recommended that the permit be modified to include the fields described above. It should also be noted that the Town is currently experiencing a serious solids storage/disposal problem, due to the Town's largest land application site's owner abruptly dropping out of the program. Therefore, it is important that prompt review be given this request to avoid WWTP noncompliance due to an inability to remove solids from the treatment system. Signature o f __1 - I1z__ Water Quality h:\nsdr�ndsrW taylors,slq epor{t Preparer Date ional Supervisor Date Town of Taylorsville Land Application Sites Table of Contents Section 1.0 Permit Application Form Section 2.0 Attachments Section 3.0 Site Specific Information :.................................. ............. ........................................... .......................................................:.......:::::::::...:::::::::.. Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites Section 1.0 Permit Application Form Wheelabrator Water Technologies Inc. Sio Gro Division State of North Carolina Dept, men of ':Environment'- Health', �and �-,Natural � Resource&,. -Division_ of F,,nviron.Managp mental.-ipe,n,t',, Non-Discharge,.,Permit ,,Application Form. (THIS FORM MAY BE PHOTOCOPIED FOR USE AS AN ORIGINAL): LAND -APPLICATION OF RESIDUAL SOLIDS, - Ms application is intended forixesiduals which Willb6 regulated tinder 40 Cf�k Part ;5'03 I.: GENERAL INFORMATION:' 1.ADDIiCarlt'Sname. (please,spec the name of the municipality, corporation, individual, etc.): Town of Taylors.ville, North.:--, Carol'fna'',W'astcL%W'ater-T'rea.tmObt - Plant` 2. Print Owners or Signing Official's name and title (the person who is legally responsible for the facility and its compliance): David M., Robinette,_Public,Works Director- -,3-.-"Mailitfg-ad(ifle'-s's-,,--20,4--�Ma-in--.,Ave.nu.e Drive-, NC City-:--Tay1-o-rsv--fl--1 e zip: 28681-'-ii' Telep 704 632.22.18 Fax 704.632.7964 hqne Number:( Application Date—.-__..Aqg_qat...20, 1996 5. Fee Submitted: S-40&;-0 0 ---'---[The permit processing- fee- should -be -as -specified in 1-5A-NCAC2H-;0205(c)(5)J 6. Specify, whether, these residuals will be lapd, applied to: agricultural lands, forest, public contact sites, reciamitibri'sit6s-,"-(Please-be"I be-disti'ibiiied*-'f(jt.-w� "i3 �la-,--.or,'h'o'm';e--g�a'rdeb use, the application for the . "DISTRIBUTION OF RESIDUAL SOLIDS" should be completed rather than this p ,2p lication.) ? V, 7. If the alternative for residual disposal consists of "surface disposal" as defined under .,jq,CFR Part.503,T1696,complete the application titled "SURFACE DISPOSAL OF RESIDUAL SOLIDS. Please identify if ibere is any storage of residuals in a surface impoundment or disposal tbrujandfilling,,PcpL : .... . 8. For Cla-ss13`Residuals (or Class AiResiddals to � be:land-aVp liedcon,adedicated.site);"ple,e.spetify,,Oc,numbe pf.acreson-,- which residual solids are to be land applied under the authority of this permit: 4- 267,.r-5-_ 'D'f0p0sed):'38'5' 0 acres I.,,-pipposc4.iD,this.a�)ph,catLon:- acres; to (current r r. 6, n- t, and ounty(ies) Whererdsiduals7vdll be land -applied: Alexander; l,­_App1_catio;,Nq!-.(willte peted"b.yPEM): 2. Specify whether project is: new; renewal*; X modification *,For renewals, complete all sections included in the application, in addition, please submit updated cumulative loadings for the ten ('10),pblititahts andIiipaai6d"o'wheri'a'greementtor!:i�� 3. If this applicidon;';is,beifigsubtnitt6d.�as.,',a result,-of:a repew_aj;Qr,mqdtftcatjqpjo an,exisLing permi ..Iist.the existing permit number. WQ0006 1 906 and its issue date November 13, 1992 FORM: LARS 06/94 :Page. 1 of J-§ k 111. FACILITY INFORMATION (attach" additional pagei for additional sources of residuals): 1. Name of facility where residuals are generated orr prepared- Town of Ta y 1 o r sV ij 1 e" - WWT P 2. Facility permit number: NC002627.1' facility permit Bolder: Town 6f -Taylorsvi.11e 3. Specify whether facility in Section 111. 1 is owned by: -federal;_ private; state; X local government. 4 4. Specify, facility design flo:,t�".'­30 mgd; facility average daily flow:" 4-00 mgd; Ngesi�er',(aerobic) Type of residual storage: Volume of residual storage: 300,000 gallons Length of residuals storage at facility: qfl days (the Division requires a minimum 30 days storage in units that are separate from treatment system, i.e. not in clarifiers, aeration basins, etc.); Maximum storage time of residuals between application events: 90 days. Estimated volume of residuals: 85 (dry tons/yr.); 5. Are there any other storage facilities other than the above, currently on site:. Yes, X No. -- If Yes, please identify: 6. Facility contact (person familiar with residuals preparation): Brian Eades 63M280 7. Facility contact's telepbone-.ziumber: -8. Location of treatment facility:--Mi nni gan-- Lane- State; NC Al.pxandp'r' County­ 9. Mailing address: 704 Main Avenue Drive SE, Taylor-wille'. NC 28681 10. Latitude: 35' 54' 25" Longitude: 8? 10' '00-11 1-1. SpSpecifyX, fy the source of the residuals....., i. treatment.6fdomestic wastewater, J.,treatment ofjndusuialwastewater; other (explain): Attach an explanation of either the treatment process, manufacturing process, or how the waste is generated. Provide full and complete details of the entire- process. 12. Does the facility which generates the residuals have arn­=appioved pretreaiindnt program?'--L Yes;-'-: No., This includes facilities which are classified as a "Class I" facility (any publicly owned treatment works required, under, 40 CFR 403.8, to have an approved pretreatment program or any facUity t-r--ea-tin-g'-do-"m"e's'tic'-s-ew-a-'ge- that is classified as "Class by -the appropriate federal or -State -authority.) - RESIDUALS' INFORMATION '' (attgcb-. -:'add itibrial, pages - .for -additional sources :of­:r.esidu.als): Information for Hazardous Waste (RCRA) Determination. The information requested on the limitations specified below pertain only to those resid6al . s that are ge. nerated from A municipal wastewater treatment facility- with industrial -contribution or active pretreatment program and from any other treatment facility with wastewater sources that include industrial sources. a. Are any of theresiduals coyered.byti-s application listed in 40 CFR 261_31-261.33? -Yes; X No. If Yes, list the number(s): b. Do the residuals exhibit any of the four characteristics defined by 40: CFR 261.21-261.24? Yes; X No. Attach laboratory results for the Toxicity Characteristic Leaching Pr­6cedure Analyses,- Reaictivity.j- Ignitability, and Corrosivity for each residual. Note: If the following constituent levels (as ,determined by. the Toxicity- Characteristic Leachifigproceduie'Analyses) are - " exceeded in the residuals or if the pH of the residual is not within the range listed below, ' owresidual is by, the definition A HdzAidofit waste:` Chemical analyses must be made:to Minimum Detection Levels---. Arsenic Benzene FORM: LARS 06/94 5.0 Barium 0.5 Cadmium Page ' 2 of 18 HIM 100.0 1.0 t.. Carbon tetrachloride 0.5 ChlOrobeaieBe `` 100.0 Chromium 5.0 m-Cresol Cresol 200.0 200.0 1,4-Dichlorobenzene 7.5 1,1-Dichloroethylene 0.7 .Endtin::.;, :!. .: ,. ; : - " - 0.02 Hexachlorobenzene 0.13 Hexachloroethane _ _ . „_ .3.0 Lindane.:.;__....... 0.4.. Methoxychlor;< : .. ; . .10.0' Nitrobenzene 2.0 Pyridine 5.0 Silver. .. •: .. 5.0 Toxaphene 0.5 2,4,5 Trichlorophenol,;;,. 400.0 2,4,5-TP"(Silvex) .. 4.0 pH, (2:1 vol./wC): 510 s.u. - <12.5 s.u. Chlordane , . 0.03 Chloroform ` ` . `6A o-Cresol "' `: 200:6 p-Cresol 200.0 2,4-D 10.0 1,2-Dichloroethane ..-0.5 2,4-Dinitrotoluene 0.13 Heptachlor (and its hydroxide) 0-ON Hexachloro-1,3-butadiene 0.5 .. ..... 5.0 .... -Methyl ethyl ketone::.. ' 200.0 ' Pentachloropheno] 100.0 Selenium 1.0 Tetrachloroethylene 0.7 Trichloroethylene 0.5 „ .,,. ;..2,4,6-Trichlorophenol 2.0 .: Vinyl 0.2 NOTE: IF ANY OF THE -RESIDUALS MEET° THE DEFINITIONS `OF AHAZARDOUS WASTE, AS'�-I4O'rED 'Ilv EITHER "A OR " $ ABOVE, A` 'PERMIT' CANNOT- _BE_ ISSUED FOR THAT -RESIDUAL AND IT SHOU.LD:'NO.T"BE` INCLUDED AS =PART OF THIS 2. For each residual, please attach a complete chemical analysis of the material: 3hu- analysts must,be comprehensive enough to, completely_ characterize the.residual,and:must, be based upon;a review of_the;processrthat,,generates,the material. If the facility that will generate the residual is not yet in operation, the characterization -must be based on similar existing facilities and projection based on the type of facility. The analysis must include a minimum of the following parameters .,, and any. other known and suspected contaminants that are tributary to the system.., IH Arseiric Molybdenum J Calcium : Phosphorus . Cadmium Nickel Magnesium Potassium Chromium _ <<.. Selenium- Nitrate -Nitrite, taste, _. _.... _.,..,.= , :-;� r.:._ .: , Nitrogen Sodium . e "um , Nt . Copper Zinc " %.,Total Solids: T1W Le Aluminum pH.: _,, Mercury Ammonia -Nitrogen Plant Available Nitrogen (by dalcu non) 3.. Wastewater residuals shall not be applied to the land if the concentration of.any llutant in the residuals exceeds the ceiling concentrations specified in the table below Spectfy the pollutant concentration `ufthese residuals (attach lab.analysis): - � Pollutant"` 'Pollutant Ceiling Concenfrati'on :(uig/kg); ; `t'poll utant:Concentration (mg/ Dry Weiebt Basis "'" kg) E �, -eight Basis Cadrhium S5 D: :`Chromium`` 3000 " 86. " ":.Copper-:.,. 4300'.. ;.._.-.. _, 17.2:.:_ Le--6d .:r:., . _ ... 840 i7:..: . Mercur 57 Mol bdenurrl° 75 , :; .. ND.:<.... Nickel. 420 34 ; Seleruumt 100:. 1 16 ;7500 FORM: LARS 06/94 Page 3."of 18 �r V . PATHOGEN AND VECTOR ATTRACTION REDUCTION INFORMATION (attachadditional pages for additional sources of residuals): 1. In accordance with 40 CFR Part 503, a residual cannot be land applied if it does not meet one of the following alternatives for Class B pathogen reduction. B1 Please specify a, bl,.b2; b3;,b4, b5,or;c.from below (submit all lab analysis, test results and. calculations): a. at least.seven residuals samples should be collected at the time of use and analyzed for Fecal coliforms during each monitoring period. The geometric mean of the densities of these samples will be calculated and should be less than 2,000,000-most probable number. per: gram"of total dry solids, or less than 2,000,000 Colony Forming Units per gram of total dry solids. b. the residuals must be treated by one of the following "Process to Significantly Reduce Pathogens" (PSRP). 1. Aerobic Di2estion = residuals are -agitated with air- 'or oxygen to maintain aerobic conditions for a mean cell residence time and temperature between 40 days at 200 C and 60 days at 15° C. -_ 2. in z - residuals are dried on sand beds or on paved or basins fora minimum of three months. During two of the three, months, the: ambient. average daily temperature is above 09..C...- = - — 3 Anaerobic Digestion-'residtial's'are ,treated.in=the.absence of•air,for;a.mean cell residence time and temperature between 15-days ae35°.0 to"55° C and-60,days-at20° C 4 Comp so tine - using either the within -vessel, static aerated pile, or windrow composting methods, the temperature of the residuals are raised to 400 C or higher for five days. For four hours during the five days, the temperature in the -compost pile exceeds 550-C ._..:: 5. "'rime' StbiLiation - suffcieiit lime is added to th'e'residuals to raise the pH ofahe,'residuals to 12 after two hours of contact' c. The residuals shall be treated!by`a'pr`ocess that is'eq'uivOl ntto a' Process to Significantly Reduce Pathogens" (PSRP), as determined by the permitting authority, based on an evaluation of the recommendations provided by the Pathogen Equivalency Committee. 2. In addition;'when residuals are being land applied, at least one of the following vector attraction reduction requirements (a, b, c, d, e, f, g; h; i, or j) described below -must be meta Specify the letter(s)''of,the-vector'attraction reduction equiremeiit that have been met (submit lab results, test T,. ," results and calculations): "Any'variation of the below must be described in full detail and attached. a. 'A�robic or'Anaerobic'Dt ion The mass of volatile solids are reduced'by.at least 38°k , Volatilesolids;reduction is measured between 'the 'resi us, prior to stabilization, and the residuals ready for use or disposal. This criterion should be readily met by,properly designed and operated, anaerobic digestors' but -not as'readilymet by aerobic digestors. 'Treatment facilities with aerobic digestors may heed to meet the vector attraction reduction requirement through 18c or b. Anaerobic Digestion - If 38% volatile solids reduction cannot be achieved, vector attraction reduction can be demonstrat,ed'by further digesting a portion of the previously digested residuals in a bench scale unit for an additional 40 days at 30° C to 37° C:' If, at the end of the-40 days,- the volatile solids are reduced by less than 17%, vector attraction.reduction is achieved.. c. Aerobic Dig ,, ion - If 38% volatile solids reduction,cannot be achieved, vector attraction reduction can be demonstrated by -further digesting a portion of the previouslydigested residuals that have a solids content of 2°k or less in a bench - scale unit for an additional at-20° C.---If;,-at the end of the 30 days, -the volatile solids, are reduced by less than 15%, vector attraction reduction is achieved. d Aerobic Digestion -The spec oxygen uptake rate (SOUR) shall be:equal to,orless than.l:5 $tilligrams:of oxygen per hour per gram of total dry -solids at 200'C-=;'- . e. . Aerobic Processes.-_The.temperature-of the residuals -for -at least 14 days shall be -greater than 40° C. During this time, the ay eraQe temperature shall be greater than.45q C,_......._,.___,...; _._ f. Alkaline stabilization - The pH of the residuals is -raised to 12 or higher by alkali addition and, without the addition of more alkali; remains-at,12 or higher for 2 hours and"then at 11.5 or higher for an additional 22 hours. FORM: LARS 06/94 Page. 4 of 18. , g ping 1 6d"cnIi' not t tabdized solids and & -total solids of - that 1&.1 . contain uns which are generated u�16'6r'greater -di" th materials is not �p,A primarywasteWater, treatment process, shall be Blending wi o er allowed to achieve the tot, solid -,percentage.. h D13dn Z fun stabiliz ed soU&YThe total'solids of residuaji that "contains -'u"n"S'tait)Mzed Whi&ire­kenerated in a .primary ,.i�aste.w.a,t..a,. apal.rn.ent process , shall be equal to o gre,ater than 9.0 Blending with other materials is not allowed to achieve the'thtal si:81ids"06tcentage."' i Injection - Liquid residuals are injected below the land surface, with no significant amount 6ff6iduals present on the 1AM,'surfaceafter 1-hour :unless ,:the residuals are Class A for pathog eq, reduction In this case; the -residuals shall be injected within 9-hours after being discharged from the pathogen treatment process. , into the soilyd n ehburs of application, %qfitati6n ­;Residwas:tbit are:gwface laiid-applied shall be incorppm- unless the residuals are . Class A for pathogen reduction. In this case; theresiduals ihall.b,e.mq9r .incorporated within-8 hours after (Bcharga 'frbni:thd',pathogen'tr'eatment-process�4�,-,., - VI. RESIDUALS �`TRkNS PORT J See P I'Wn -:,&f Operation 1�­� b U the residuals bgkUv�q (Iijk,pr tru&S, ett.,?,?,_ H wwi q4 tq, Oq ap . - . , ­�.. P _� ,plication sites ­1 S - 0pera on ,.,, 2. What type�.of-equipm6twill be udliz&d:fbr1and application?.: pe, Kan -of 01 the application of the residual be controlled to ensure that there is proper distribution over the site? 'Plaw1of Opera :4, � 4. Will the -land application operation utilize a contracCor whospecializes i" ;-R6sidbals`kanageiiieniv or" will the permittee -management the'pr6gram.21 Periiiittee�,,',If�a-.coritraCtori�5,utiliz_ea. d-_,prpyide the name of the firm, a contact, address, and telephone number: Bio Gro Division of Wheel abrator4it' F'Technolbqies 'I c. X 'b '�.-VIIr3-SITE-'"E';VALUATION- ANI)r-)RECOMNIENDED-LOADING RATES: 'A "t, o g"fi6s"ifMb�-tsedf6r-.Iaiid'a� i n -La.]: I win- 2 s perm-it1pplication. [please Attach map.(s),�� Applkaii6fi Area [aci6s] Maximum Slope T Note: If more than ten (10) sites are to be covered by this -application, please attach a form listing all of the sites along -with. the information listed below::::-, r a. A vicinity map must be attached. This map must...::show -the Jocation of each site in relati6h to. at least two geographical references and major intersection (numbered roads, named streams/riyers, etc.). FORIM: LARS 06/94 .page`' 5` of 18 b. For all new or modified sites, a detailed site location map must be attached delineating both total and buffered acres. This map must be drawn to scale with topographical contour intervals not exceeding ten feet or 25% of total site relief (whichever is more descriptive) and showing the property lines; all existing wells, all surface waters and drainage ways and all dwellings within 500 feet of the land application areas; and all buffers. Tote: At least the following buffers must be maintained. If residuals are sprayed on the sites, larger buffers may be required 1. 400 feet from any habitable residence or place of public assembly under separate ownership or which is to be sold for surface residual application, 200 feet from any habitable residence or place of public assembly tinder separate ownership or which is to be sold for subsurface residual injection. 2. 100 feet between the disposal area and any public or private water supply source, all streams classified as WS or B, waters classified as SA or SB and any Class I or Class 11 impounded reservoir used as a source of drinking water t 3. 100 feet between any surface residual application area and any stream, lake, river, or natural drainage way, 50 feet between any subsurface residual injection area and any stream, lake, river, or natural drainage way.+ 4. 50 feet between the residual application area and property lines for both surface and subsurface application (if the original permit was issued with the buffer distance to property line as 100 feet, updated maps must be submitted and new acreage delineated for the buffer to be reduced). 5. 10 feet between the disposal area and any interceptor drains or surface water diversions (upslope). 6. 25 feet between the disposal area and any interceptor drains or surface water diversions (downslope). 7. 25 feet between the disposal area and any groundwater lowering and surface drainage ditches. t SPECIFY THE NAME OF AND CLASSIFICATION OF THE CLOSEST DOWNSLOPE SURFACE WATERS (as established by the Environmental Management Commission) TO THE LAND APPLICATION SI7E(S)• USE THE ATTACHED INFORMATION SHEET (PAGE 9 OF 18) TO OBTAIN THIS INFORMATION. Tote: The maximum slope for land application of residuals is 10% for surface application and 19% for subsurface application. 2. For each land application site, attach a soil evaluation by a soils scientist (the evaluation must be signed by the soil scientist) which addresses soil color; the depth, thickness and type of resuictive,horizons; the presence or absence of a seasonal high water table or bedrock within three vertical feet of the deepest point of residual application; pH and cation exchange capacity. if the depth to either groundwater or bedrock is less than three feet, please also attach a demonstration, using predictive calculations or modeling methods acceptable to the Director of the Division of Environmental Management, that the use of this site will not result in the contravention of classified groundwater standards as contained in NCAC 2L .0200. In no case shall the separation be less than one foot. This report must be signed by the soll scientist and submitted with application. 3. For each site, please attach a project evaluation conducted by an agronomist including recommendations concerning cover crops and their ability to accept the proposed loading of liquids, solids, nitrogen, phosphorus, heavy metals, salts and any other contaminant know to be in the residual. A part of the agronomists recommendations must be a crop management plan. This plan must determine the crops to be grown on the site(s), when they should be grown and how they should be harvested and marketed. This report must be signed by the agronomist and'submitted with application. 4. Attach a representative soils analysis of each site. The soils analysis shall include the following parameters, along with any other significant parameter that has been shown to be contained in the residual: Standard Soil Fertility Test (which includes): pH Phosphorus Potassium Acidity Calcium Manganese Magnesium Zinc Copper % Huatic Matter Sodium Cation Exchange Capacity Base Saturation (by calculation) And the following Metals: Arsenic Lead Nickel Cadmium Mercury Selenium Cbromium Molybdenum 5. In order to assist DEM in the review of the proposed loading rates, please complete the calculations contained in the anachment titled "Calculations Work Sheet" (beginning on Page 11 of 18). if more than one residual is to be covered by this permit, additional worksheets must be attached. FOR11. LARS 06/94 Page 6 of 18 VIII. GENERAL INFORMATION: 1. Five .(5). complete copies of thepermit application and five (5).copie,s of all required supporting information, including * will cover le rs must su te application ap, cati n package w .l . be returned as incomplete-. 2. Please explain how access to the land application sites,,by.both people and animals, will be controlled following the application of residuals: See Operations Plan I ' I 'a. Anima"Isshdl'n-otl);e=graiedonthe landapplication 'sites 'within 30 days after the application of residuals:, b. Appropriate measures must be taken to control public access to the land application sites during the active site use and for 12 months following the last application event- Such controls may include the p . os4g .'of signs'indicating the activities being conducted at the site. 3. -PleaseexPlain the procedures that will be used to establish and maintain the buffers during the application process (i.e. will , the sites be flagged): See Operations Pl,an 4. Please attach an executed "Agreement For the Land Application of Residuals to Private =L-ands; - ior"ea''cl -land-applicatibb'gite that is not owned by the applicant. Apopy, * of the DEM approved form is attached. If the applicant wishes to use a different form or a modified form, pnor appr:&V: afmus 5. Each application site must be assigned a site identification number., 6. Attachments may be utilized to provide the information that is requested in this, application form; however, if attachments are utilized, their location should be so indicated on the application form. hAll atta&hir umW6d to corresp6bd to the individual parts of the application that require the attachment. If the attachmentsare t part of a, iargelr"docimeq a table must be provided that lists the locations of the required information.* Applic nt's :Cer f] �cation,: UAV I'D '0 Nanest that this application for: _-­`10 W."/_ .0 -Zh&k_�u,' lit — has been reviewed by me and is accurate and complete to the best of my knowledge. I understand that if all required parts of this application are not completed and that ii-altreqiftd: supporting'.-i ;nfonnatiooii--a4d;. tt2(p4pdnts X&--,not,-,included;1 this -#pp ck-a e pa 9 will be returned as incomplete. Signature Date ? THE COMPLETED APPLICATIQNTACKAGE, INCLUDING,.,ALL. SUPPORTING INF,ORNIATIO-N.AND MATERIALS, SHOULD BE -SENT -TO THE FOLLOWING ADDRESS: 3, NORTH ,CAROLINA DIVISION OF ENVIRONMENTAL MANAGEMENT WATER QUALITY SECTION PERMITS AND ENGINEERING UNIT- :POS.T_OFFIQE .BOX_29535, R_A,LEIGH, NORTH -CAROLINAr,�;27626-.0535 TELEPHONE NUMBER: (919) 733-5083 FAX NUMBER: (919) 733-9919 FORM: LARS,06/94 Page 7 of 18 0. essing, of this -applicationwill not be initiated, until five (5) copies of all of the following to,fi 'b(5)*'6ojpi6s of the c6rnp'leted i iplicati6n!"form. If qW.s. 116vebebn submitted in addition v . -.1.. '-fr- '11i package, 'pl . ease' explain. ny of the below, items have been excludedom c 1. Is--a_general , lo.catio.n.map--included? Y.E.S. X or NO , Is a site map, (drawn---to-isr-ale)l.;.included-.wh.ich rdelineates -totalan ._0,reA:.. apres., and line shows all property lines, buffers, existing wells witliih 500 feet, topography, drainage - I -features, and 'any "surface "-w-at9 waters X YES or'NO 3. Is a vl�c- -,y-nip,enciosea-wh,ioh'cle,ady:L ation 'with -respect to State,roads .and -named...Su.r-face, waters?_-, ..... . . . ..... _V, d hic fif" ­th':'j"'R` 1. Is a signed. soil sq'ientist report include.,,vy..., s _t�o,qe e,jq�qw... a) field descriptions of texture, color, and structure, b) depth and thickness of soil horizons,, c) presence of any restrictive soil horizons or layers, depth to ;of high151eA '' ,,- water ta--ii-' e hydraulic con ud ivi y,.,-.- f) recommended lo_a:din'g­7 ate -for th' 'sit bi YES X or NO 5. Is a signed agronomist's report includ.e*d which identifies the crop;__Cqhd--I­0ading .--recommendations. for_ N7P-nK?; 8. �'I9AhW­0,--fo'1 p ana "M t- 'rit�PIan,lin-cludedTin,r-thei-a'opVicationipackage?..jz.d.-.,�-�.r.ii?,..f,,-,it--,r geme YES X or NO 7. Has the Land Owner's agreement - be-'e--n-- co'm'-'p-l-e'--t-"-e-d-a--n-d"--si'g--n-e-d? YES )( or NO �� �.­ I". �: � i -_, 1 ` - '' 0, ­ "" ­­ .)(5 98 B.- Ap"prop6ate fee in accio'rd-�n-db with',15,A NCA _,2H`.0205(c Xbff. ebril - di�y 1A0 New Applications, Modifications or Late Renewals $400.00 Timely Renewals without Modifications 0 0—, 3 YES X or NO 9. Five (5) copies of all reports, evaluatibhs7t,­agreem-enf s,-�sOl5porting calculations, etc. must be inclued as a part of th6.-'-'aoolidAtion.-pAdkage.v�! -'.. :_'l >­ . A. .. .— .. __ _:`i` a Si. = � 4.' �.��.. �...:.`.. .. .. _ , '_ .... . FORM: LARS 06/94 Page 8 of 18 UCr11VK 1"IUUICtJV1LLr- KU rdX • (V4-000-0U4V mug 1 7o 10 - 10 r. V11VL Aug - O 1- 15A, P) P . 02 This form must be completed by the appropriate Regional Office and included with the submission of tine opplication package. INSTRUCTIONS TO APPLICANT in order to determine the classification of the watershed in which these land application activities will be located, you are required to submit this form, whit items 1 through 8 completed, to the appropriate Division of Environmental Management Regional Water Quality Supervisor (see attached listing). At a minimum, you must include an 33" by I I" copy of the portion of a 7.5 minute USGS Topographic Map which shows the subject surface waters. You must identify the location of the facility and the closest downslope surface waters (waters for which you are requesting the classification) on the submitted map copy. The application may not be submitted until this form is completed and included with the submittal. 1. Applicant (Ply Specify titC name of the municipality, corporation, individual. or other ): 2. Name and Complete Ad of Applican[: , ► ■ r d- (9titb 1; Q. nr Ls r&&244iU]40 A110Ou& B__ qx. zi • z-� fig! ' City: State: p• Telephone umber. 3. Project Name: o N a -E 4. Volume of residuals to be land applied: dry tons per year 5. Name of closest surface wants: 6. County(s) where land application site is located: 7. Map [tame and dau: Q a• T Qr , IV e. 14 20 8. Applicant Signature: TO: REGIONAL 'WATER QUALITY SUPERVISOR Please provide me with the classification of the watershed where these land application activities will occur, as identified on the attached map segment: Name of surface waters: 4!91"'IelWk CI-2 e _ Classification (as established by the Environmental Management Commission): 601 . Proposed Classification, if applicable: Signature of mgional office petaonrtel: G'�L Date: i1, FORM: LAORS 02/95 Page 9 of 18 c -3, -CALCULATIONS-WORK- SHEET' is work sheet is designed to assist the Division of Environmental Management in -reviewing' this'application as expeditiously as ssible. Its preparation in a complete and'kcnrate'ffAriner is critical to -this review. For permits that cover multiple sources of residuals or different residuals from the -same-source, use additional work sheets,..- A List the specific residu'iil°`thit'is'cdier6d-'-,by-ihese ... calciii -a' do fis­,(place­-or process of origin) Town of Taylorsville, NC aerobically diges-ted­§judge. : ry.,-.Wm pf,-t14§ residual.to be land,ap liedeach yearl What are.the,-.,toWA p d' Total DryTons = Gallons of Residuals* 9b­lj Sos"­*'9.341b`sjg o produced annually A,00 2,000"Ibs./ton Total Dry Tons 8.34 lbs./gallon 100,­ 2,000 lbs./ton Dry. ' Tons'per year If the quantity..of residual will vary sRgh-ific­a-nay,­oi,.if -theiv. will be -,,a largot'. initial application, please attach a detailed explanation and provide calculations for each variation. B. Complete. the following calculations to establish the portion of the residual that is made up of carious par % Total Solids • 74 (PLEASE DOTE THAT ALL`CONSTITUENTS`ARE'.! TO BE -IN -TOTAL CONCENTRATIONS) ' PARAMETER mg/L r % Solids (Decimal)_ mgfkg -(dry mvt.) x 0.002- = lbs./dry ton Arsenic--- .-005994---- 81 x _0,002 00.162 CaCadmiumND x 0.002 Chromium .6364 .0074 = 86 .172 Copper 1.2728 .0074. 2'-- ­3 jOIRONJI .344 1258 0 0022 034 Mercury =-.39 x, 0.002. .00078 Molybdenum `6001 Nickel .2516 - ­0074, = 34 x 0.002 = .068 Selenium .008584 .0074 1.16 x 0.002 = . n0232 Zinc 2.5604 34.6­­. x 0.002 = .692 9,9..g.. .0074 = 13500. x 0.002 =27 -Anu-nonia-N Calcium 4.4 --.-0074. 6000.'" x 0.002 =12 Magnesium 19.98 -.0 074 27�.Q x =5.4 "N2 0 189 x 0.002 .378 9'* Pff6,sPh0fu 1,0-21--1., 86 -:6074 =13900. slum 45.14 .0074, --6'100 100 2 -: 1-2. �.2 F5.48 V.1w, - .0074 10200 i U.602] = 2 0.'4197.2 -Sodium TKN. �29.64 .0074 ' 9.86Q0 ' I 'X 0 001 FORM: LARS 06/94 Page 11 of 18 C. Plant Available Nitrogen, (PAN) calculations and land application area requirements: CONSTITUENTS MgfKg DRY WEIGHT TKNI -:'.1'.98600' 'AMMONIA-N.....P., 13500' L�NO3-NO2-N 18 1 9 -.-.l-..-.-Mineralization-Rate.(MR) 30 % f :1j:jd jjsij�d1or-doinestic wastewater -treatment (These values can be established for the specifl. S' dtial& & au t v' u'es,cali residuals. If actual values are established, attach the documentation. The default values are as follows): Unstabihzed Primary and Secondary Residuals Aerobically Digested Residuals 30.%_ Anaerobically Digested Residuals 20% .: Composted Residuals 10% (If the default values are used, arch an explanation -as to why. -the sp6dific.chQseq default value is appropriate.) 2. Complete the following calculations for the ap e. note, the Mineralization application. proposed (Pleas Rate [MR] -should -be utilized in the following-Eak i66 is. a decimal) TAN for:Surface t_;.Applica.tj o.n PAN= [(MR) x (TYN -NIH3)] +.5 x (NH3) + (NO3-NO2-N-) n 3 X.. Qh� PAN 3G 98600" 1 5 0 0' PAN = 32469 -PPM Dry Weight "tRAN r -S Application. - PAN N027N) (N 7 .7;[(?�R7) , x , (TKN N"H91 -+-(NH3) 03 �5G0­_1­1­­_­_­­_ 18 9 3 .30, "798600 )+ P, 3. Total PAN Total dfY ��'of residual to be land applied per-�y�ar: s Total�Y -g -PAN in -,pounds-, 4 - - TAN inl� j/k -Dry Weight) X;2000 Po4ds I Ton per"dry-ton 1,000,000, ­(PAN,in PPM Dry Weight)--x 0-002 ,-,- 78.43 Pounds/Dry TonNear AID'in Pounds Dry Ton) x Total tons of residual to be land applied _...._.____Total_PAN_in_ pounds-_-,.... _.x­1....85- --dtl.y 4. 6 67-.2 -PoundsNear ? ... ..... -Due totfie:.,fact+tfiat- organic nitrogen is �miner�,slowly-over.,time,,the-amount.of.nitroRenthai comesavailablein years -, - application must be taken into consideration when calculating application rates for the -su sequent th -k§ i4act-on-loading rates.: Show the idjuited Pan years.-.:7,.bis,,,bein:g, the- case, plea -se attach an evaluation o is-Tact6fand foratleast five years: The -maximum adju-sted1rinual PAN is . ............ See -at-tachment_nurnber- 8__1_.A.____._-"--­-, FORM: LARS 06/94 Page 12 of 18 P 'Crop lforma"on `on nitrogen uptake per Year,-,, (Division Recommendations) (Provide, for the Crops Specified) ?4 1.W, Crop(s) PA'�6VS-/icredyear) , 'PAI(i6'siac�roy.i 2 Alfalfa 200 Bermuda' Grass (Hay;;Pasture) 120— Com (Grain)--_-... 1 60'.- Corn (SUagp),,,:,,-:.-, 200 Cotton. 70 a Fescue 250 Forest (Hdkd I w "d &-S6ftwood)­ Mao 7 100 Small diair`f (Wfiek,-barley,oats) Sorghum, Sudex (Pasture)-._-_. Sbighumi, Sddex:-(Silage)., 220 200 ---Tim othy,'.Orchard, -&..Rye. Grass -20.0 Please prop ide the basis for the uptake rates `-used-if Vfdf&rit1E9i'DiVisi= Recommendations: v-t 4. 5. Total acres needed to land apply &'poiinds-bif available -nitrogen 'calculated above Total acres neededJtotal b6u'-n s'df Man t available ntf6gen-(PAW `64'1&of nitrogen needed for 6r6*:-` 3 arares­. e -3- -nE!e d Jli Minimum ln acres need ed based on most restrictive PAN acres - ------ ill "e;" alue for the crop to be grown that has the lowest nitrogen uptake rate per -acre:- must ,v per -acre...- ­ If there are various crops -that -will only- be- utilized for-cCftain,sites, -please attach the calculations for each site and detdrmine the total heeded acnis`6sinp the format outlined above. Calculate Ahe_.S_odWm..,A d s,pfp 0q;x__F4#q OAThis section -must �,.-.completed.in mg/l, to, convert:.. mg/kg x %.solids [as,A,jdecim all m,g/l##), Milli Equivalent ,+ [0.5, i -(Ca'MiUi -Equivalent-+,Mg-Milli-Equivale .5 ..... .... F4WvaIenrW6ight7 ....... _;­­­ Milli Equivalents -of Ion- - SODrUM (Na) 76.48­ 13'i = -8..28 v.. 97­d_.. r: CALCIUM (Ca) 44.4. (mg/1) '2,22 ;j $, MAGINT-srum (Nlg)19 - 98 (mg1l) 12 1.66 SAR = 2.35 FORM: LARS W94 Page 13 cift-18 J. ip�_idual or site,please.- attach. - a V, If calculation - sheets are being completed for more.,-Ahan one---,r summary, sheet that bring the results of all the calculation sheets to one point. PE. aermngtle,", site:,, The -lifetime pollutant -loadings shall not be exceeded. The' site life is determined by calculating the numWof -years that the site can receive the residual without exceeding the lifetime pollutant loadings. The site life calculations will be based on the most t.t6t' ' d ' �naximumt'&Yth�' re diiiis Ian applied r6sMddV6bf6p'pl;in't'dVgldble'iiitMgen (PAN) requirement specified and the sit- si' annually —Therefore, in.the table below the Tons of Residdals to be Applied/AcreNear will be calculated as., 1.._Most.restncuve_crop.based 9R;4e plant available nitrogen (PAID fescue requirement: 250 --,---Associated--plut-available nitrogen (PAN) requirement'- 2. --Minimum 'acres "needed '-based on most restrictive PAN (as found in C.5 above) e, - 3. Dry Tons of Residuals to be land applied per year 85 .. ........ (lbsJacre/y6ar)" 26.6 acres 4-.—Tons-of-Rt--siduals-to-be-Applic,d/Acre/Year= - TonsNearof Residuals to be land Uplied'- Minimum number of acres required for land. application V ...---Tons-of Residuals. to.-be.Applied/Acre[Year 3.2 CID ;t " If any -of the _application,si.Les�amjOe loaded at greaterihhfi the rate specified abovqji,.p!COe;,sPe4;ifv the loading ate and 6xPlain Tons zf-Residuals.-to-be-App4e4cVAqrefYear (different from above) - - - - - - - Explanation: t Z. 7777 -.7 n i Zb-1 Ij ..-In-the-table-below I -thQ-hip-best annual I ding. (Tons of Residuals to be Applidd/Acre/Year) specified above, will be multiplied by the lbs./dry ton of each pollutant as found in B above. The Site Life can then be, determmed Site Life (Years) = AlloWOle Lifetime Loadings (Ibs./acre) Projected Pounds to be DiD ie cre ta � Pollutant Residuals to-bgT Applied pei --Acre-per-Year- Ibs./dry. ton -of each (asfoundinPartB lApplied/Acre above) -d, Pounds to e. fYea r - 'Allowable Lifetime, " Pollutant Loadings. (lbs./acre) `­'Sfie Life (Years) Arsenic '1. 2 .00162 .005 36 =7200 Cadm"I'U"M" -3-2­ -007 0 Chrornhitn-' -°­ '550 - -2677, =.4867 7 CoppeT_ ;3,2.*,. .44 ..3 1,338 1216 Lead 3.2 034 267 Mercury 3.2 .00078 09,2 J 5, =7, .5,QQ __374 1780-,-., �= UM Selenium ._.0022 .007 89 _. I 12, 714 _13.2 Zinc 13.2. "_ 22­ 2A 98 I f3 5" Compare the nine (9) pollutants above and determine which pollutant that will result in the sbortest life for this site.., The Limiting Pollutant is Zinc The Site Life is` 1135 years. Also see attaC1hMent--huft16:6r 8. FORM: LARS 06/94 Page, 14 of,48 North Carolina Division of Environmental Management AGREEMIENT FOR THE LAND APPLICATION OF WASTEWATER RESIDUALS TO PRIMATE LANDS 40mittee: TOWN OF TAYLORSVtLT F 'ontactPerson: David Robin,�~te Eahllir Waretc AddressofPermittee:204 Hain A-v ,i Dr. S E. Taflo:svi11e ,': 23031 Phone ( 704) 632- List of wastewater residuals to be applied to these lands: Liquid Aerobically D i e t e 3 Site ID Number: , See Site Specific _Ln,fo Field Number: See site Soecific Info '.ocation of Land to be used for residual application (include map for each site): Owner of Property used for residual application: �.. : sE e S i c e Data .essee of Propcny (if appropriate): See Site Data Land use or cropping panerns: Intended use or disposition of crops: Not for Direct Human Consumption a * ! • * * ! • i t * * a 0 • * * * * * * * * * * * * * * * * * * * * a * * * r * * • * * a * • t f • * t f Che undersigned land owner or his representative hereby permits iereinafter referred to as the Perminee, to apply the above listed residuals onto the land at the location shown as described herein in accordance with the restrictions and stipulations as given below. The andowner or his representative receives, in consideration, full use of the nutrient value of the applied _esiduals while the Permitt.ee receives, in consideration, the use of the land described above for the disposal of wastewater residuals. This agreement shall remain in effect for the length of the Division of ;nvironmental Management land application permit and shall be renewed each time the land application nermit is renewed. The undersigned land owner or his representative and the Pennittee agree to abide with ie following restrictions and stipulations until such time as written notification, given thirty (30) days in advance, modifies or cancels this Land owIlgr's Agree, ment . ;otifcation of cancellation of this agreement shall be immediately forwarded to: TORM: LARS 06/94 Division of Environmental Management Permits and Engineering Unit Post Office Box 29535 Raleigh, North Carolina 27626-0535 Page 15 of 18 STIPULATIONS: 1. The landowner or his representative hereby authorizes the Permittee, County and State Officials or their representatives to inspect each parcel of property prior to, during, and after residual application and to established monitoring facilities on or near the application site as required by the residual land application permit. 2. The landowner or his representative authorizes the Permittee, County and State Officials or their representatives to take necessary soil, surface and ground water samples during the term of, and twelve (12) months after termination of, this Agreement. 3. The Permittee will provide each landowner or his representative with a copy of the land application permit as issued by the N.C. Department of Environment, Health and Natural Resources (NCDEHNR) Division of Environmental Management (DEM) for the land described above prior to commencement of residual application. The NCDEHNR-DEM permit will specify maximum application rates, limitations and other restrictions prescribed by the laws and regulations. 4. The Permittee has provided the landowner or his representative with information and data concerning the program for land application of residuals to privately owned lands which includes an analysis of constituents of the residual, residual application methods and schedules for typical cropping patterns and a description of the equipment used by the Permittee for residual application. 5. The Permittee will furnish each landowner or his representative with a copy of the results of each soil analysis. 6. The site shall be adequately limed to a soil pH of at least 6.0 prior to residual application. Residuals may be applied to sites with a pH of less than 6.0 provided a sufficient amount of lime is also applied to achieve a final pH of the lime, residual and soil mixture of at least 6.0. 7. The landowner of his representative will inform the Permittee of any revisions or modifications to the intended use and cropping patterns shown above prior to each planting season to enable the Permittee to amend this Agreement and schedule applications at appropriate periods. Within the limits of the NCDEHNR-DEM permit, the owner or his representative and the Permittee will determine residual application rates and schedules based on crop patterns and the results of soil samples. 8. Crops for direct human consumption shall be harvested in accordance with the conditions of the permit. 9. The landowner or his representatives or successors shall adhere to the provisions of this Agreement for a period of eighteen (18) months from the date of the most recent residual application. 10. Appropriate measures must be taken by the Permittee or Land Owner (Lessee) to control public access to the land application sites during active site use and for the twelve (12) month period following residual application. Such controls may include the posting of signs indicating the activities being conducted at each site. 11. Specific residual application area boundaries shall be clearly marked on each site by the Permittee or Land Owner (Lessee) prior to and during application. 12. Should the landowner or his representative lease or otherwise permit the use of the land by a third party, the landowner shall be responsible to insure the third party agrees and complies with the terms and conditions of this Agreement. 13. The existing lessee, if any, of the site agrees, by execution of this Agreement, to comply with all provisions of this Agreement. FORM: LARS 05/94 Page 16 of 18 r 14: 'Phis'Agreemem shall be binding on the grantees, the successors and assigns of the parties hereto with reference to the subject matter of this Agreement 15. Animals should not be grazed on residual applied lands within a thirty (30) day period following the residual application. Application sites that are to be used for grazing shall have fencing that will be used to prevent access during these periods after each application. 16. Prior to a transfer of this land to a new owner, a permit modification must be requested and obtained from the Division of Environmental Management The request shall contain appropriate fees and agreements. In addition, a notice shall be given by the current landowner to the new landowner that gives full details of the materials applied or incorporated at each site. 17. Any duly authorized officer, employee, or representative of the Division of Environmental Management may, upon presentation of credentials, enter and inspect any property, premises or place on or related to the application site and facility at any reasonable time for the purpose of determining compliance with this permit; may inspect or copy any records that must be kept under the terms and conditions of this permit; or may obtain samples of groundwater, surface water, or leachate. 18. The landowner shall not enter into any additional waste disposal contracts or agreements with another municipality, contractor, or other permitted entity for the land specified by this Agreement. The land application of any additional wastewater residual sources, other than the residuals specified by this permit, is prohibited. RESTRICTIONS: FORM: LARS 05/94 Page 17 of 18 y have read this land owner's agreement and do hereby grant permission m y to the Permittee to apply slud9presidual to my lands as specified herein. Land Owner % //D % mo Date NORTH CAROLINA, COUNTY, I, the undersigned Notary Public, do hereby certify that:D �� - - G personally appeared before me this day and acknowledged the due execution of the forgoing instrument. WITNESS my hand and official seal this day of l®wtw , 19� J, 444;& j� 4-- INWAIRY PUBLI My commission F2 ®oa SEAL: 4 CIP eG W? -J3 41 9 toy 0 °q� I, ��•b O have read this land owner's agreement and do hereby agree to abide by ZL the stipulations and restric ' s as specified herein.. Lessee Date I, 04V I R0 4 W eft have read this land owner's agreement and do hereby agree to abide by the stipulations and restrictions as specified herein. Permittee Date FORM: LARS 05/94 Page 18 of 18 I, have.read this land owner's agreement and do hereby grant permission to the Permittee to ap y sludge/residual to my lands as specified herein: f, Land Owner _ .. _:`Date _... . .. .... .. ....._., ,,, .. NORTH CAROLINA, . G i" OUNTX • r I, the undersigned Notary Publicdo;hereby certify that s _ , ... personally appeared before me this day `and acknowledged ,the due execution If the forgoing instrument. W SS my;hand and official •,seal -thus day of ,.19 — My commisston,Epr 1-4 SEAL:. ��� J.,�0``� o� have read this land owner's agreement and do hereby agree to abide by the stipulations and res ictions as specified herein. Lessee fZ (e7 Date ####*#####*##*####*#***#####*###*######*#*##**#**#*#*### 1, A V),0 (�o f N C -f have read this land owner's agreement and do hereby agree to abide by the stipulations and restrictions as specified herein. Permittee Date FORM: LAORS 02/95 Page 18° of 18 Rufb 1.1 "7b 10r-.3GMrl IVPA■ Vr fM 1l_V.1Jv 1LlL Aug-08-96 09:6 A P.01 J � have Hasa Ws land o s agreem eat and do 0 Wy 5 v6l � Pu 4101piaaidml�tcq t � to m' hods as spec" hw - Land Owner • Dltte . NORTH CAROLINA, ®ter COUNTY, I. the undetsipaed Now Public. do bemby Ce.a fy that personoy appm d betas tag this day and acknowledged the due exeCutiOO Of the forgoing instrument. WMESS my hand and of&W a d this day of NOTARY PUB C SEAL: A,�� J 0 la L%Cj :fin'---- - ................ II i• .wd &I. 1®!d &-A A. Stw..6V .,w+tw •hiM I.y tb• `etruliea• .rsaleer r ��+. - LCSSEC Dim r ✓ 2 y f uave rm wu =a gwwrs agm=c u mu oo =my &vs e w awe Toy she WPM" xuwkdm • sPccilW herein. Penniaee +-- FOA14l. LAOFA *V" rose Is of We Town of Taylorsville Land Application Sites Section 2.0 Attachments Attachment 1: Owners and Addresses Attachment 2: TCLP Test Results Attachment 3: Biosolids Analysis Attachment 4: Treatment/Stabilization Process Attachment 5: Operation Plan Attachment 6: Soil Scientist's Report Attachment 7: Agronomist's Report Attachment 8: Site Life Evaluations :.;:::.;;;:.;:.::.;;:.;:.;:;:.::.;:.:;.:.:.:................................ . :.......................................................................... ..... Wheelabrator Water Technologies Inc. Bio Gro Division Town of Tavlorsville Land Application Sites Aftachment 1: Owners and Addresses Robert Lynn Marshall Routa4. Box4O1 Taylorsvi||e.NC20O81 704.632.6190 William H.Marshall 728Hastings Hill Road KernenviUe.NC282B4 910.788.8955 Donald G.Payne 45OOPaul Payne Store Road Tovon;vUm.NC28681 704.632.8223 Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites Attachment 2: TCLP Test Results Please note that TCLP testing is required only once during the life of the permit. Wheelabrator Water Technologies Inc. Bio Gro Division PAR PAR Laboratories; Inc. 2217 GRAHAM PARK DRIVE LABORATORIES, INC. P.O. BOX 411483 CHARLOTTE, NC 28241-1483 704/588-8333 April 1, 1992 Reference No: 92 1134 Made For: Bio Gro Systems 12701 Lancaster Highway Pineville, NC 28134 Attention: Robert Hamilton Analyses of: Submitted sample for TCLP Marked:. Wastewater sample from Taylorsville Received On: 3/19/92 Analyses: pH Value 6.5 Corrosivity Non Reactivity Non Flash Point (°F) >200 Ignitability Non (ppm) Arsenic <•5 Barium <10 Cadmium <•1 Chromium <•5 Lead <•5 Mercury <•02 Selenium <•1 Silver <•5 Paint Filter Test Free Liquid U _ ._ .....��-��--.^ >>-:,. ,..:air r c nr ... -.. -�,- .• 'y . ! '.1 : /. 'F� � .. ., R PAR Laboratories, Inc. caBORATORIES.INC. 2217 GRAHAM PARK DRIVE P.O. BOX 411483 CHARLOTTE, NC 28241-1483 704/588-8333 Reference No. 92 1134 Continued Benzene Carbon Tetrachloride Chlordane Chlorobenzene Chloroform o-Cresol m-Cresol p-Cresol Cresol 2,4-D 1,4-Dichlorobenzene 1,2-Dichloroethane 1,1-Dichloroethylene .2,4-Dinitrotoluene Endrin Heptachlor Hexachlorobenzene Hexachlorobutadiene Hexachloroethane Lindane Methoxychlor Methyl ethyl ketone Nitrobenzene Pentachlorophenol Pyridine Tetrachloroethylene Trichloroethylene 2,4,5-Trichlorophenol 2,4,6-Trichlorophenol 2,4,5-TP Silvex Vinyl Chloride Respectfully Submitted: PAR Laboratories, Inc. John S. Rice Laboratory Director a <.05 <,05 <.003 <10 <.6 <20 <20 <20 <20 <1 <.75 <.05 <.07 <.013 <.002 <.0008 <.013 <.05 <.3 <.04 <1 <20 <.2 <10 <.5 <.07 <.05 <.2 <.02 <.1 <.02 k Town of Tavlorsville Land Application Sites _ - ) ' ��K EASTERN LABORATORIES, � �m m~ »�»�~�n u~nun� ����oxn����u~n ��xu��u~ INC.no��� 7621 Whh8piO8ROad ° Richmond, Virginia 23237 ° /804\743-9401 Fax No. /804\271-6446 RO62-3O6 ACCOUNT 45469 PAGE 1 REPORT NUMBER BIO GRO SYSTEMS INC 12071 LANCASTER HIGHW1jY HWY 521 SOUTH PINEVILLE NC 28134 L�B NUMBER = 41190 S")MPLE ID = 1 OF 1 RESULT PARAMETER ( % ) ---.... .... -.... .... .... .... .... .... .... .... .... .... .... .... .... -------- SOLIDS NITROGEN (TKN) PHOSP�ORUS POSIUM SULFUR C�LCIUM M�GNESIUM SODIUM IRON MANGA�ESE COPP[R ZINC AMMONI) NITRO[ 1*1103-NO2 NITROE C�DMIUM CHROMIUM NICKEL LEAD AtL TOWN OF TAYLORSVILLE ROBERT HA.MILTON COPY TOH" ANNAPOLIS ` BIOSOLIDS ANALYSIS REPORt� `^ DAT[ SAMPLED 03/14/96 '�ATE RECEIV[D O3/18/96 REPORTED 03/21/(p6 DETECTION RESULT LIMIT ofNI",LYSIS (MG/KG) (MG/KG) ANALYST Df�,TE -.... .... .... .... .... .... .... .... .... -.... .... .... .... .... ... .... -.... .... ------- METHOD REFERENCE ---------------------- O~74 740O 1OO J C M 03/18/96 SM 254�� 9.86 986OO 1OO KCS O3/19/96 EP� 351^3 1^39 139OO 10O DHC O3/19/96 EPh 365^4 O^61 610O 1OO DCN O3/19/96 SW 846-601O 01-69 6900 10O DCN 03/19/96 SW 846-6010 0^60 600O 1OO DCN 03/19/96 SW 846-6010 0^27 2700 1OO DCN O3/19/96 SN 846-601O 1^O2 1O200 1O0 PCC O3/19/96 �W 846'6O1O 655O 1 D C N O3/19/96 S� 846-6011,31 71 1 DCN 03/19/96 SW 846-6010 172 | DCN O3/19/96 SW 846-6O1O 346 1 DCN 03/19/96 SW 846-6O1O 13500 1OO LDR O3/19/96 EPYj 350^2 �N 189 1O LDR O3/19/96 EP� 353^1 ND 1 DCN 03/19/96 SW 846-6010 86 5 DCN 03/19/96 SW 846-6010 34 5 D C N1 03/19/96 SW 846-6O1O 17 5 D�N O�/19/96 SW 84�-6010 (.L A /1) 1 �LL VALUES EXCEPT SOLIDS AND TSS ARE ON A DRY WEIGHT BASIS. �-�p �- �^ ^ PAUL C^ H^ CHU C/ NPRM0� �ONE� Our �por�mm�on�amnrme�muv*oand nnnodonno|use mour u�nm.�mmay not uo�pmuu�dinwhole o,mpo�.nor may any memmmuvm����n �-~~ work, the results, or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization. oopynom1e7r R062-'-306 REPORT NUMBER A & L EASTERN AGRICULI JRAL LABORATORIES, INC. 7621 Whitepine Road - Richmond, Virginia 23237 • (804) 743-9401 Fax No. (804) 271-6446 ACCOI.JNT 45 469 PA C7 2 C'iRC) f:iYSTEMC) T'NC: .120 '1 1...ANCA:iiT'I:::l I-1:1:f1FIWAY 1-1WY 21. SC)LJTI"I F, IN NC; 2 G 1.34 I._('11:<. NUMDI":F, :::: 41.:1.90 f S 14, M P L. E :I: Li J. 0F' :1. T C)WN OF 1.16I YI...C)F;SV .* L.I...17. It10ED01...:I:j .*) ANoL.Y�'T,'1:i F;I:::F'C)F0, xlE T,E:(:.'r:F.C.)N F1E:Sl.Jl...'T RESULT I.-1:MI'T ANAI...YS1: , I"AF;AME::'rE:F; ( ) (MG/KG) (11Ci/KG) ANALYST DATE'' AFL 1;C'1DF.::RT 1'9Ai''1:1:1...'T'CIN C;OF'Y TC) T ANNAF'CA.A.* S DATE f:1r'1MF,I...IH'D 033/14/96 rIF,1TE: RE C:I::::1:4'E,D 03/:I8/96 >IA'T1i:: 1::, 1': 'I'f:::JCI i?:7/.'.:L/tr6 ME"1'I"IC)S:! F';I:::F,E::I;is A{,tiL:.N.It.: 0.811. 0.4 SIt.' N () .3/?',>/ `IF1 t"1 ? L. , -`t 6....7()61 ME:::r;C:LJRY 0.39 1 L'!C:N 03/20/ 6 C),W 8'46 -74 1 SF::I...I:::N:F.LJM J..1.6 0.:1. rlC:N 0:3/20/96 SW f346 -T7 41 PI -I (;a'T'AN'D(ItF"D UN:I:'PS / . 0 M 03/:I.`:1196 I:::f') :I.:`.;U.:I. i A...I TAJN' ("AF;S:t(:)N(1i i'I::: E U 0171 7:1. ?0 100 KC' 0:3:'I.9/96 A:TM ; ():r () L.°11,1: :I: . k{. 'V 1.) :I. ((f L. I l I i (i :3 ,' :I. ' !'r 6 <:i i S ' ;: 4 () Ci f:)FiCiANA, Cl C)GI:::T'd A".i 2:100 K(f: (? 3!:I.'i'/9F> t' Al...l'::l.Jl...l'1TI:::J(.! MC)I...Y;E D1:::i"!I.JM NT) 5 :CIC;N 03/J. r /{> 6 SW 1346 6()J 0 C",F-II._01:111,1)::: 6 300 .1. L.1.1 03/:?:I.!96 ;alai 4:'.i()0--- i::l... SI,JI...F'A'T.1::: 5340 :LO '1C.:M 0:3/ ':L/96 f:iW E:)46"'9O Z),3 1 AL.L. VALUES EXCEPT SOLIDS AND 'rSS ARI" ON A DRY WEIGHT BoSTS. i RP A L WJ1 CC. 1"I. CI-ILJ Nthe M N ONES Our reports and letters are for the exclusive and confidential use of our clients, and may not be reproduced in whole or in part, nor may any reference be made t work, the results, or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization. Copyright 1977 AV& 4.E.ASTPERN.; ilkGTRICUL". '..)-tRAL imc. 7521 W,tiitEpine Rbad - Richmond,.Vitbinia-23237 (804) 743=9401 Fax No. (805)" 21-1-6446 fi462-306 ACCOUNT .15469 1=•fiii� ;i REPO T�NUMBER J• l &:YQ- GRO SYSTEMS INC 1,2071' L.ANCASTER •HIGHWAY HWY :521. SOUTH• PINEVILLE MC 28134 LAP NUMBER = 41190- SAMPLE IU - 1. OF 1 RESUL•I PARAMETER > OWfd OF T6YLORSVILLE B1050LIDS ANALYSIS REPORT DETECTION a; c�lL 1 LIMT T CMi;: iir i rMG/tiG) ANALYST ROBENT 146MILTON COPY TO ANNAPOLIS DATE - AMP'Lt:G 03"14/96 DATE PECk IVED 03/ 18/` 6 LTA YE REPORTED 43i 21 /yl<, ANALYSIS DATE METHOD f�C1=cREMCF SOLIDS NITR0c;C.N t TKN) .+ c�. %�i 9,t,b )4ljQ•.r it3hG0 t00 -�- l Ci l:)G •:• l.ii tip+ " 5 0G PHOSPHORUS I a 19 1.3YO0 100 PHC POTASSIUM 0161 6100 I00 Llctq 0:3/1?/96 Ellei 31,r;.4 SULFUR 0.69 6900 100 TJcN 03/19iY6 Sid B46-6010 CALCIUM 0,60 6000 100 t1CN 03.119/r 6 sw 846-6010 AO MAGPlF_rTUM S 0.27 27Q0 104 DCN J3/19/9d SW' A46-60i0 E 1102 10200 100 PCC 03/19/96 SW 046•-6010 IRON 65:0 1 03/19/96 5W --b0i 646 a MANGANESE DCI�! 03/19/96 SW £i4—601 Ft 172 1 DCN 03/I9/96 SW 646-6010 ZINCCOPP ZINC 346 1 UCN 03/19/96 SW '94-6-6010 AHI[O�liA NNITROGENi .,:3�� 13547 100 DCN 03/19/96 5W 8�6-b010 NO:�-N€l2 NITROGEN 169 lb L11IR U3/19/96 EPA 350.2 I 1 LOR 03119/96 EPA 353.1 -HROM1Fi �iL R6 5 i►cm 03/19/96 'SW 946-6010 NICK 34 1icN 03/1.9/9d SW 8A6--6010 LEAL:EL LkAtt 17 a UCN 021/19/96 Sw 04-6-6010 Li: M r13/ 19/96 c- rW •046=•-610 10 it:t VALl!ES EXCEPT •SOLIFIS AND TSS ARE nN A 1IRY WFI(:I-Ii• ZzACY4-' i `_ H. Ow repots and tefthis are for The exciusive a M coniidenti5! "W of aim clients, and may not be racxacWme in wWo of in IsaA, nor may arty ►ef e,enoe be mado fo T,w Work. the results, oatne o«rpany in auq aduatisiny, r,aws retpace. or other pantie :•."'0u&% erue.Ms wnhnut obtainiN our for written Qutiw�izalion, . cc�rYr�eT ��n .. l r 7621 :WhiteOirie'-Rdad •';i chaiono, V+rSin(a 23237 (804):743-9 .0 F$x:No-.(904)-27 =6446 PAGE..- REPOAT NUMBER ara ona - sYs'rEms -ING 1207-t'I.-ANCASTER 'MMAWAY HWY:. • 52'1: SOUTH PINEVILLE NC '20134 LAB NUMBER - 41190 SAMPLE TD - 1 OF I RESULT PARAMETER y y TOWN OF TAYLORSVILLC BIOSOLIDS ANALYSIS kF.PORT DETECTION RESULT LIMIT (MC/KG) ( MG/KO) -ANAL Y51' ANALYSIS D6TE ROGER-C tfAMZI..'Cot4 COPY T01 ANNAPOL i a PATE SAMPLED 03/ 14/ 96 DATE RECFI.4r.ED .4.3/f L4/96 DATE RKPORIEI= 03/21/96 METHOD REFERENCE FcSEh'IC EkCUf�Y �:■.E31 0.4 VC'N 03/20/9b 5(J 9 i fi- /461 E"N I UM 0.39 1.. 16 0.1 0. i. IICN � 03/20/96 �' sw �I � � 74 71 N (STANPAREt• UNITS) 7.20 D 2 ALCIUM CARBONATE EQ 0.71 7100 100 r'fi7 03/19/96 EPA 154.1 OLATILE SOLIDS 67.41 674100 100 KC+IS i_DR 03/17/96 ASTM Cb02 RGANIC NITROGEN 8.51 65100 100 KCS 03/19/96 sM 254OG OL Nii s 03/19/96 CALCULATED HLORIDEUM 6300 r1cN 03/19/96 GW 046-6010 ULFATE ATE: 340 1 10 LItR 03/21/96 sm 4500-CL JCM 03/21/96 SW 844-9030 L VALUES EXCEPT sOLYDS. ANL TSS ARE ON A DRY WEIGHT !)ASIS. � ��.'LtH. ' Lf/ Our roporls and kiters we to the exdrr�ive �r+d oorrhderrrra! use of ow c4w". and may rat be repmduc-ed inwttoie or in paL C • N 0 R MAN L)ON'E S %"k, the resutls� or the oompww w arty adreAi9 v, mews reteasa, or c&cf put�lk: annouwernenty without obteiR'IrOr may any tteNererrCe be made to the • n9 (wprwrWmen aulhonzalk CopyrVu Ig" l Town of Tavlorsville Land Application Attachment 4: Treatment/Stabilization Process Wheelabrator Water Technologies Inc. Bio Gro Division STABILIZATION METHOD The Town of Taylorsville Wastewater Treatment Plant employs aerobic digestion. PSRP could not be verified by the conventional treatment processes using time and temperature. However recent data has shown that plants with long sludge age or no primaries do have acceptable pathogen densities for land application. In order to show this we have verified reduction in vector attractiveness and fecal analysis as outlined in EPA./625/10-89/1006 Environmental Regulations and Technology, "Control of Pathogens in Municipal Wastewater Sludge". As shown on the attached lab data sheet we have verified that the digestor waste sludge has less than 6 average log density necessary to comply with PSRP equivalency. This attached sheet also verifies that the reduction of vector attractiveness through the SOUR test. The digestor waste sludge has less than the 1 mg. oxygen/hour/g TSS intake at 20 C required for PSRP equivalency. At this time only one sample has been collected for this verification. We are in the process of collecting additional samples and forwarding that data within the next three weeks. In the meantime, we ask that you continue the review of this application and we will forward the additional data shortly. M mist/Philbrook Z0'3Jdd 6260 ZbS b02- 1 SZ:6t Z6, b gnu e •spTTosoTq aa� .. spot ate TpsodsTp aoTad at:g. uaaq 9-eq buTTTT=puet puE spaq buTLaQ •uoTgeoTTddp puej o4 paeomaa aq TTTM aagsabtp ate uzoa3 sabpnTs pu-e queTci ate 7o p-eat; eq4 oq paAomaa as 'iTzM -ZagsabZp ate 4zoa.4 qu-oaQ • aags2bTp aug. o.:. *paeoucaa aae xaT9:zseTo atM tQoa9: sabpnTs ags-eM (sagnuTm pC-SZ) aagme'Ra 4oe4uoo auTaOTRO at4 grbno�--qq 1 Ta.eez4 saagZM asatqL (buT1440s X-T2puoaas) saaTaT-reTo 157q-4 0'4 ua-gq pue uTseq uoTq-cave auo o-. MoTg: saagTTg: a5at:4 moil sTeT-m4lex •saa4IT9 buTTxoTaZ Z a74 04UT paKsnTg uau4 sT s-rgy •dn XOlaq uoTTeb 000T - 008 a a09 MGTTE ?z[M sa-4 buTsop oqut pebzE-qosTp sT sxueq Z asstr4 moz-Z MOT-Z '4tmnT-J9:H ' sxLmq .73oqarI Z oguT PagngT-r4s?p K"ETenba sT puE xoq zaggTTds E og.uT usaaos a*eq ai:rq qbnoaz� s-taAe-74 'auTT TTE;--no uTem ate. -qbrnoag4 KgTTToe3 queTd ate szaatza aa4EMagstM Biological & Chemical laboratories, Inc. Post Office Box 40 Granite Falls, North Carolina 28630-0040 (704) 396-4770 stonier: Town of Taylorsville Date/Tlme Collected: 6/17/92, 3:30pm 204 Main Avenue Drive, SE Sample Collected by: B. Eades Taylorsville, NC 28681 Date/Time Received: 6/17/92, 5:45Dm 0: N00026271 Date Reported: C 6/26/92 AnalysIs Units Influent Effluent Upsireem Downstream BOM-Day mg/L I1 1,2 COD mg/L 1 Fecal Coll. /100 rn! 1 T.S. Residue mg/L 1.2 Ammonla, N. . L, mg/L 1 Nitrogen, T. mg/L _ 1.Z Phosphorus. T. mg/L 1 -PH SU's i Oxygen up a e i Digester - 200C_ Waste Return - 200C I Imhoff T Ink - 200C Init, ai 3._4 Initial 3.6 Iri t 'L. al 3.1 Ites 5 minutes 3.4 5 minutes 3.5 5 min 3.1 J _ 10 minutes •4 3 10 minutes 3 ; 10 mi�utes 3.0 � I i'E: Date analyzed pe rs on laboratory worksheets since 'Preservatives: lain anab/ses may 6 ,< dormed on different dates dueo 1. Coo! 4.0 C° _hold time requlremer�ts. : , ' 2• pH 2.0 H2SO4 • l i 3. pH 2.0 HNO3 `.. ✓. `... •, Approved by: 4. pH y 12 NaOH � � � - LaFa tte A, Gragg, Lab Director 5. Zn Acetate + NaOH o pH ? 9 z X X I X ` 1 DRYING 1 REDS �L H 1 / _ I � H JIUDGC DRYING BEDS CIIIUCMT i I /+ LNT SIAIIGN N•.S Ne4 Nn J I Ne.2 N¢ I Ne.6 LSV-2 /+ J/ /F O DBV-1 ----_— .m DBV-2 — DBV-3 e'—I-- DBV-4 OBV-5 —— §DBV-i k ---__— — —_ __ _— p y-7 O V-B ADVe�I 0 V-9 — 4 v-10 / Ne FILTER I - 4• \� 1 X k .}.T+ �'`(�� � D 7 1 11IMARY $LODGE PUMPMO STATIDI/ / �♦ ° e / Y \ e'_ / � PSV-I,PSV-2,PSV•3, ! 'a. p♦ // PSV-4,PSV-5 k \ RPV-2 RECYCLE I • V-1 PUNPIND STATION RPV-I, RPV-5 t,_12___,.•/ // ^ ,di t`° •DI •cry � r /// RPV-4 4..P,g-3 � FSp�••v scvu..._ OPERATIONS a UILDING / fSPLITTER— / Boxr ® —�SS__ -- -INFLUENT K I SAM SCREEN �. aw•Ns•n ►e.•p•• N Nr•w SPv-2 / N¢ I ♦ / / / ABV-2- �yf DOSING �' bOCL CHAMBER Off' �♦\ // \\ .p�//// \ \ TRICKLING FILTER N¢Z I . _ __ r • --- f- r ' f I I FIGU R IOM e ¢ ¢ -CLARIFIER- ¢ eCV-3 (TYP) NEW LINE EXISTING LINE ----- WATER LINE _W_ _—W-- I ADV-9,ADV-9ADV•ID 2• 1DV-1,A.V•.9:AlV•II 7 ADV•5,ADV=G,ADV-7 I 4 ADY•5 AOV•6 ADV•7 Town of Tavlorsville Land Application Sites Attachment 5: Operations Plan A. INTRODUCTION This Operations Plan contains detailed operational procedures designed to comply with applicable regulations and guidelines. Additional procedures and constraints have been incorporated based on Bio Gro's previous land application experience with the ultimate objective being a land application program that safeguards public health, surface and groundwater supplies and provides an agronomic benefit to the project area. B. GENERAL DESCRIPTION OF PROJECT Aerobically digested sludge and sludge from the Imhoff Tanks generated at the Town of Taylorsville Wastewater Treatment Plant will be land applied in a liquid form. Sludge will be loaded at the wastewater treatment plants and transported in tank trailers to permitted land application - sites. Bio Gro Systems will land -apply the sludge on approved sites in accordance with the operational procedures described herein and at rates set in the permit. C. LAND APPLICATION PROCEDURES 1.; `Sludge Removal, Transport, and Application a. Sludge removal. f Sludge will be removed from the Imhoff tanks or aerobic digesters at the wastewater treatment plant with a submersible pump. The sludge will be pumped through a six-inch flexible wall hose to a loading tower. The flexible wall hose will be connected to rigid PVC pipe at the loading tower. A remote control switch will be located at the top of the loading tower to control the power source to the pump in the holding tank. The tractor/tank trailer units will pull under the loading tower with the tank trailer being filled trough a hatch located on top of the trailer. 1 b. Sludge transport and method of land application. Sludge will be transported from the treatment plants in tractor/tank trailer units to approved land application sites. The transport trucks will deliver the sludge to a high -flotation land application vehicle J stationed on the field receiving sludge. The sludge transfer will be through a suction.hose t .WU ". :L. -A . . .1 SI 11.1i ._t4a7,T sV7zf - . .. ..cam and the land application vehicle will perform all sludge distribution. Sludge distribution on the sites will be uniform throughout the distribution area. To ensure adequate control of the application rate for each site, the equipment used for spreading the sludge will be calibrated by measuring the amount handled on a known square footage. While the rate of discharge from the application vehicle is fixed, the speed of the equipment can be adjusted to maintain whatever flow rate is desired to achieve specific application rates. The mode of application will be subsurface injection or surface application followed by incorporation by discing. Injection and incorporation will not occur on pasture and hay fields or on cropped fields where the farmer has adequate crop residue and wants to maintain a no - till or minimum tillage system. The method of application is selected based on the crop that is being grown and the tillage practices being employed by the farmer. Since ,farm operators typically rotate different crops and tillage practices in a specific field each year, it is not possible to determine exactly what method of operation will be used on each field at -this time. Prior to each application, a representative meets with the farm operator to determine what crop is being planted and what tillage practice is being employed for a particular field. If row crops are being planted using conventional tillage methods, the sludge will be injected. If the farmer is planting the field using no -till practices or the field is in pasture or hay, sludge will be surface applied. If there are any sites that have seasonal high groundwater conditions that preclude incorporation, the sites could be surface applied. However, a better alternative would be to place seasonal restrictions on the site and conduct operations only during periods when seasonal highs would not be encountered. Equipment to be used on the project includes: 1. Two -to -three totally enclosed, watertight tanker trucks of 6000-6500 gallon capacity. 2. One high -flotation land application vehicle of 2000-4000 gallon capacity. Operations will be discontinued during periods of inclement weather and will not be resumed until sufficient drying of the fields has occurred. The truck units will be inspected, licensed and appropriately marked as required for the purpose of transporting the sludge material. C. Storage Town of Taylorsville provides storage for the sludge during non -application periods in the existing digesters and Imhoff Tanks. 2. Site Operation a. The sludge will either be injected or surface - applied followed by incorporation through discing. Discing and injection will not occur on pasture and hay fields or on cropped fields where the farmer has adequate crop residue and wants to maintain a no -till or minimum tillage system. b. The amount of sludge applied will.be limited to the annual allowable dry tons per acre as required by the permit for the site. C. Buffer zones will be observed as follows: 1. Distance from traveled surface of roadway: 25 feet. 2. Distance from on -site residences of the landowners receiving sludge: 100 feet for surface or subsurface application. 3. Distance from any habitable residence or place of public assembly under separate ownership or which is to be sold: 200 feet injection or surface application with same day incorporation; 400 feet surface application without incorporation. These distances may be reduced to 100 feet with written permission of the resident. The form used for obtaining permission is included in Attachment 1. 4. Distance from any well with the exception of an approved groundwater monitoring well or a well that has been permanently abandoned in accordance with state regulations: 100 feet. r State of North Carolina Department of Environment, Health and Natural Resources Division of Water Quality James B. Hunt, Jr., Governor Jonathan B. Howes, Secretary A. Preston Howard, Jr., P.E., Director A4 RJ DEHNFi N.C. DEPT. OP September 24, 1996 ENVIROMIFNT, HEALTH, 6 NATURAL RESOURCES SEP 90 1996 Mr. Charles Mashburn, County Administrator County of Alexander DIVISION of EIIVI?OP►u1EIlTAL h',AIIAGEMENT 255 Liledoun Road MONESVItLE REGIONAL OFFICE Taylorsville, North Carolina 28681 Subject: Permit Application No. WQ0006906 Town of Taylorsville Land Application of Wastewater Treatment Residual Solids Alexander County Dear Mr. Greer: The Division of Environmental Management has received an application from Town of Taylorsville for the land application of residual solids from the treatment of wastewater for two new sites in Alexander County. This Division will ensure that all federal and state regulations are enforced. If maps of the sites are needed, please contact Mr. Rex Gleason , Water Quality Supervisor, in the Division's Mooresville Regional Office at 704/ 663-1699. Should you desire to comment on this application as it relates to your interests, please do so no later than September 25, 1992. If you have any questions, please contact Mr. John Seymour at 919/ 733-5083 ext. 546. Sincerely, / John Seym ur �' Permits and Engineering Unit cc: VN400resville Regional Supervisor Alexander County Health Department P.O. Box 29535, Raleigh, North Carolina 27626-0535 Telephone 919-733-5083 FAX 919-733-9919 An Equal Opportunity Affirmative Action Employer 50% recycled/ 10% post -consumer paper 5. 100 feet between surface sludge application area and waters classified as WSII, WSIII or B and 100 feet between the application area and the Mean High Water Level of waters classified as SA or SB; 50 feet between subsurface sludge injection area and waters classified as WSII, WSIII or B; and 100 feet between the application area and the Mean High Water Level of waters classified as SA or SB. 6. 100 feet between any surface sludge application area and any stream, lake or river. 50 feet for subsurface injection. 7. Distance from groundwater lowering and surface drainage ditches: 25 feet. 8. Distance from property lines: 100 feet unless the adjoining property owner concurs with sludge application closer to the property line. The form for obtaining adjacent landowner's permission to apply sludge up to their property line is included as Attachment 2. Buffer zones will be flagged or marked and no - sludge will be applied within the buffer zones. The most restrictive buffer will apply in combined situations. d. Provisions will be taken to prevent soil loss through erosion. Provisions will include contour application and avoidance of areas where surface - drainage patterns result in concentrated flow of runoff from rainfall. e. Seasonally wet areas are of concern only during very brief periods of the year with abnormally high precipitation, usually during the months of December through March. In the unlikely event that such seasonal ponding does occur these areas will be buffered by flagging. In addition, good agronomic practice requires that areas which are unseasonably wet and would produce rutting or damage to the field should not be utilized for sludge application or any other farming operation during those periods. f. The amount of sludge applied will not exceed the hydraulic capacity of the soil at the time of each application. In no case will it exceed 27,000 gal/acre (one acre inch) per day. If a subsequent pass across a field is necessary to achieve the desired application rate, sufficient drying time ' will be allowed between passes. g. operations will be discontinued when soils are saturated and will not be resumed until sufficient drying of the field has occurred. h. Sludge may be applied on frozen ground that has crop residue sufficient to prevent surface runoff. During such application, the maximum slope to which sludge will be applied will be five percent. i. A minimum of 36 inches of soil will be maintained between the deepest point of sludge injection and bedrock or the water table during the period of application. < - j. Sludge shall not be applied on areas exceeding 18 percent slope for injection or surface application with incorporation and 10 percent for surface application without incorporation. k. Soil pH should be adjusted to 6.5 or greater prior to application. 1. All grazing by animals whose products are consumed by humans must be prevented for one month following the last application event. This will be accomplished by keeping animals fenced out for 30 days.. M. Public access to sites which have':lhad sludge applied shall be controlled for a period of 18 months from the time of last sludge application. Since private farmland is not generally accessible to the public, this objective is usually accomplished through normal practices. n. Crops for direct human consumption with the harvested edible portion in contact with the sludge -amended soil shall not be planted for a period of 18 months following the last application. 01 Town of Taylorsville Land Application Sites Aftachment 6: Soil Scientist's Report Wheelabrator Water Technologies Inc. Bio Gro Division Soil Scientist Report ,The sites contained in this package were evaluated by examining existing USDA-SCS Soil Survey information, the soil material exposed in a series of hand auger borings and by soil sampling and testing. Other important items that were taken into consideration were depth to bedrock and seasonal high water table. Topography Slope on these sites are typical of the area of the state. The slopes range from nearly level to the maximum of approximately 3.0 percent. Topography will not limit injection but surface application of biosolids may be restricted in some areas. Soils The soils information necessary to determine quitability for the land' application of treated biosolids must address both agronomic and engineering properties of the soil materials encountered on the sites. These properties can be evaluated on a preliminary basis by examining published literature .such as that nnntained in Soil Survevs published through the Soil -Conservation Service. In addil confirm the soils soils were evalua sites with a hand locations on the represented in tt evaluated with i. properties includ horizons and prey bedrock within addition, a serif from the plow lay capacity and pH constituents. T) are contained in .ion, an actual site investigation is' necessary to information contained in the soil survey. The red by examining soil material extracted from the auger. Hand auger borings were taken at selected sites representative of the major soil types e soil survey. The soil material extracted was icreasing depth for selected properties. Those a: depth, color, texture, presence of restrictive once or absence of a seasonal high water table or feet of the biosolids application zone. In s of core samples were collected and composited =_r on the sites to determine soil cation exchange .o establish background levels for selected site .e results of the auger borings and core samples this submittal. Application Rate Recommendations The biosolids generated for this project have been tested and verified as non -toxic, non -hazardous and suitable for application onto agricultural land. Based on the analyses nitrogen and zinc are the most limiting factor to the annual application of these biosolids. At the nitrogen application rate sufficient phosphorus is also applied. The farm operator will need to apply potassium since the sludge is low in this element. Phosphorus should be added if soil tests indicate that the soil is low in this nutrient. Salt additions at these application rates do not pose a problem. In general salts are not a problem in humid and sub humid regions because there is sufficient rainfall to leach them down through the soil profile and away from the crop root zone. The soil test results indicate that the cation exchange capacity of the soils fall within the 4. 8 to q-..v meq/100gram range. Based on this the most limiting metal in terms of cumulative loading is zinc and. it would take approximately 39.9 years of annual applications to reach this level based on the highest application rate of 3.2 dry tons/acre. The hydraulic loading rate will be limited to 27,000 gallon/acre/day for liquid application. Sufficient drying time will be -allowed between applications to prevent hydraulically over loading the site. Soil testing of the proposed sites indicates that the cation exchange capacity of the topsoil material on the sites.is generally in the low to medium category. Research conducted in recent years has shown that soil chemical properties such as low cation exchange capacity are not limiting factors when low metal biosolids are applied at agronomic rates. Heavy metal recommendations contained in this submittal reflect the lowest cations exchange capacity category currently utilized to establish EPA loadings. conclusion The material proposed for application on these sites is an excellent source of nutrients. Neither biosolids characteristics, sites characteristics, nor soil characteristics should preclude use of these sites in a land application program. With careful operation and strict adherence to Federal and State regulations these sites should be excellent sites for biosolids application. Soil Scientist Bio Gro Systems Town of Tavlorsville Land Application Sites ........................ Key to Sod Boring Log Symbols = Not Encountered Note: Soil borings were conducted on the following dates: Borings 1 and 2: June, 1996 Boring 3: July 30, 1996 Soil boring locations are indicated on the site plan map. I = Boring Number 1 2 = Boring Number 2 3 = Boring Number 4 Key to Site Plan Map -.40, Well Locations Field Boundaries aSoil Boring and Number m�. Buffer Zone Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites Field No. Boring No. Depth (Inches) Color Texture AI-4-1 1 0-6 brown 7.5 yr 514 sandy clay loam 10-48 dark brown 7.5 yr 4/4 clay AI-4-3 2 0-6 brown 7.5 yr 5/4 sandy clay 10-48 dark brown 7.5 yr 4/4 clay AI5-1 3 0-6 strong brown 7.5 yr 5/6 sandy clay loam 7-12 yellowish red 7.5 yr 5/8 clay 12-48 strong brown 7.5 yr 518 clay .......... Wheelabrator Water Technologies Inc. Bio Gro Division I Sc��1 .Series:: BETHLEHEM 2.0 - 6.0 BUNCOMBE RAPID >6.3 CECIL 0.6 - 2.0 f CHEWACLA 0.63 - 2.0 F DOGUE 2.0 - 6.0 PACOLET 2.0 - 6.0 RIVERVIEW 0.6 - 2.0 Percolation Texture cec (ln/hr) meg/10 2.0 - 6.0 SANDY LOAM RAPID >6.3 LOAMY SAND 0.6 - 2.0 SANDY CLAY LOAM 0.6 - 2.0 LOAM 0.2 - 0.6 SANDY LOAM 0.6 - 2.0 SANDY CLAY LOAM .6 - 2.0 FINE SANDY LOAM 0.06 - 0.10 LOW >6.0 0.06 - 0.08 LOW 2 0.13 - 0.15 LOW >6.0 0.13 - 0.15 LOW 0.5 - 1.5 (NOV.-APRIL 0.08 - 0.15 LOW 1.5 - 3.0 (JAN.-MAR.) 0.08 - 0.12 LOW <6.0 .12 - 0 LOW 3' - 5' Town of Taylorsville Land Application Sites Attachment 7: Agronomist's Report ....:.............:::::....:........:......::::::::::................................:::::::::::..;;;:...............::.:::.::..::.:.:::.:;:.....:,.:,.;:.;,.;:.:::;::.;::.::.;::;<.::.:;.;.::.::.;:.:;:.::::.......::.::.::.:.:::.::.; .....:;:.::;.:.;::;.::;.; Wheelabrator Water Technologies Inc. Bio Gro Division Agronomist Report Several factors should be taken into consideration in determining sites agricultural suitability to receive biosolids. These factors are soils, crop rotations, loading rates and nutrient requirements. The crop types and cropping schedules are investigated prior to a site being considered as a biosolids application site. The sites in this submittal consist of row crop land (corn, soybeans, small grains) with some permanent pasture and hay land. Biosolids analysis information is reviewed to determine the most limiting application rate factor. For this project nitrogen is the most limiting factor. Due .to the low solids content of the biosolids hydraulic loading limits may also limit application rates in that more than one application pass may be needed to supply the nitrogen requirement of the crop to be grown. When applying to row crops, biosolids will be applied prior to planting or after harvest (this would provide nutrients for the next planting). Timing of application is important with permanent pasture and hay crops. Biosolids should be applied .on these crops after a.gr`azing period or hay cutting. If hydraulic loading limits require that more than one pass be made on a field in order to satisfy the nitrogen requirement of the crop being grown, the field should be allowed to dry sufficiently prior to the next application. Soil testing of the sites included -in this application indicates that soil pH 6.0-6.5 on most sites. The lime recommendations are generally made based on raising the pH to a standard of 6.5. The nutrient requirements are a direct function of specific crop needs. Recommendations found in the University System and Extension service publications for specific crops should be used to determine nutrient requirements. Application rates are -- based on the annual nitrogen requirements for each particular crop being grown. This application rate will also supply sufficient phosphorus for plant growth. In many instances such as with zinc, sulphur, and copper essential micro -nutrients are also supplied to the plant. The resulting trace metal loadings at nitrogen limited rates are minimal. Because of the low levels of metal additions there is no cause for concern with regard to concentration of metals in plant tissues. Salt additions at these application rates do not pose a problem. In general salts are not a problem in humid and sub humid regions because there is sufficient rainfall to leach them down through the soil profile and away from the crop root zone. 1 The crops being grown on the site in this submittal are primarily corn, soybeans,_ wheat, other small grains, permanent pasture and hay. There are no restrictions on harvesting and marketing any of these crops other than there shall be no animals grazing on sludge applied fields for 30 days following application. My review of the soils and crop rotations proposed for this project find the submitted sites to be suitable for the land application of sludge. B eCR Agronomist `�Bio Gro Systems o �ROBERT CERrIF,ED HAA4/LroiVAUR ee m �og� Q,o �+yr� O 9 ` "O �omt6 f49'�O�p 0 r REPORT NUMBER A&L EASTERN AGRICULTURAL LABORATORIES,'INC. 215-1086 7621 Whitepine Road • Richmond, Virginia 23237 • (804) 743-9401 Fax No. (804) 271-6446 SEND 'I0 GRO D IVIS IC TO: P S 388 P'INEVILLE, NC • 2 134- 03 3 DATE OF REPORT 08105196 PAGE 1 GROWER: ROBERT L MJARSHALL SOIL ANALYSIS REPORT A(CCT # 45469 SAMPLES SUBMITTED ROBE T HAMILTON BY: COPY T0: ANNAPOLISP MD DATE RECEIVED 08101196 DATE OF ANALYSIS 08/02196 ORGANIC PHOSPHORUS POTASSIUM MAGNESIUM CALCIUM $ODIUM ° , ° PH Cation at PERCENT LAB _ MATTER • * ** HYDRO- GEN Exchange Capacity E SATURATION (COMPUTED) BASE P1 (Weak Bray,) P2 ',,(Strong Bray) tig` SOIL BUF FER - NUMBER NUMBER ENR*.. * H % RATE ° lbs. A ppm-P RATE ppm-PRATE ppm-K RATE m-M d',RAT.E Pp 9 Pp m-Ca RATE' n-Na RATE, PP .. PH, pH meq/100 g meq/ 00 g K Mg Ca H Na ° 1_ C55 7, 6.3 140V 1 87 V H . 240 = V 230 V 180 VH c 20 R 5.7 �. 1 ■ � �. �` ■ � $.1 2. � 1.1. 2 05C58 14p VIII.7 18�s` V� 190 VH9 850 5.8 : .9, 1.5 7.8 5.9 4.7 9.0 9^-8r.0 � "a 6:Y 1r lVH:24E�0''VJ �L ! "Y F6 ;.'! R,T = V 1 6v� '17 - +Y Y {i gN 7� ')"7 ■ • .6. . 9.0 ■ q0■4 T s 1.1 ■ 8 (SEE EXHLANA I IUN UN BA(;K) SAMPLE NUMBER NITRATE NO PPm No3 N RATE ' SULFUR° " S ppm-S RATE ., ZINC Zn': ppm-Zn RATE MANGANESE Mn , ppm-Mn RATE IRON • ° Fe PP m Fe RATE COPPER Cu _ PP m-Cd RATE BORQN B PP m-B RATE EXCESS LIME RATE '',- SOLUBLE SALTS ' mmhos/cm RATE CHLORIDE, CI P pm -GI RATE MOLYB- DENUM • Mo, ppm Mo RATE ° PARTICAL SIZE ANALYSIS % SAND % SILT ` % CLAY SOIL'"` TEXTURE ° 1 .11 :M 16. 4= Vie 28 H 90 V 1 6.0 V 1 0. 2 11 N 21. 3, Vii 29 h 74 V- 8. 2 V u. 0.9 mt 3 11 M 22.7 VP 3<3• H 81 V 413.1 V 1 0.8 This repo plies to the sample(s) tested. Samples are retained a maxim thirty days after testing. Soil Analysis prepared by: A &/ETER GRICULTURAL L ORATORI , INC. NOR JONF by I v nM I IN : V ❑M LVVV (VL), LVVV (L), IVItuIUM (IVI), MUM (H), vtHY HIUH kVH), HNU NVNt (N). ---- MULI II LY I HI_ FItSUL 16 IN ppm BY 4.6 TO CONVERT TO LBS. PER ACRE P205 v ENR - ESTIMATED NITROGEN RELEASE ""' MULTIPLY THE RESULTS IN ppm BY 2.4 TO CONVERT TO LBS. PER ACRE K20 % ORGANIC MATTER AND ESTIMATED NITROGEN RELEASE (ENR) The Organic Patter content is determined chemically on the dried screened soil sample, I"{o:vever, the total organic content may he somewhat higher than reported because larger pieces of plant and adimal residues are screened out prior to analysis. Only a pat of the total nitrogen in the organic matter of a soil will become available for plant use during the growing season. Many factors such as: soil moisture, soil temperature. the soil's physical condition, and the amount and type of crop residues present all have an, effect on bacterial action. Therefore the ENR value is only a guide to the nitrogen supply available for the growing crop. For additional information on nitrogen release and recommenri'ati n guides, see pages 5-12 in our boots "Sou and Plant Analysis." Results:The results for the major and minor plant food elements are reported in parts per million (ppm) on an elemental basis. Conversions: To c:on vert to ibs'A, the type of soil and tillage depth should be considered. iftst mineral soils weigh approximately2million pounds (dry weight' for anacre ofsuit 6bito7 nchesdeep.Anacre of soil 10 inches deep weighs approximately 3 million pounds. in the past, most laboratories that reported results inib-E. per acre were considering 2 million ios. of sail per acre (resul',s in pprn x 2 lbs. per e cre). However, with deeper tillage practices used today many growers are dealing with nearly 3 million lbs .of soil per acre, :�I#IS1V��'IL+1'�ft't Results in ppm 2 Million lbs. ."of soil per acre 61,4-7 in. deep Results- in ppm 3 Million lbs. of soil per acre in 9-10 in. deep -P x 2 = lbs, per acre of P P x 3 bs. per acre of P x 4.6 Ica. per acre of P.O. x 6.9 = lbs. per acre of P20s K x 2 = lbs. per acre of K K x 3 = bs' per acre of K _ x 2.4 = lbs. per acre of K O x 3.6 ' lbs; per acre of K20 Mg x 2 = bs. per acre of iv g (• g x 3 _ lbs. per acre of Mg Ca x 2 tbs. per acre of Ca Ca x 3 = tbs. per acre of Ca S x 2 =. lbs, per acre of S S x 3 lbs. per acre of S S x 6 = Ica. per acre of SO4 S x 9 = • ibs.. per acre of SOa B. Zn, iJn, 6, Zrr, Mn, Fe, Go, Mc Fe, Cu, Mo x 2 - tbs. per acre of 3, x 3 - lbs, per acre of B• Zn, Mn, Fe, Cu, We Zn, Mn, Fe, Co. Me PHOSPHORUS Two different tests are made and reported for availability of phosphorus in the sot; sample, Weak Bray (Pt)-Thismethod determines the amount of readily available phosphorus in the soil, A level of at leas; 20 ppm of P is desired for average crop production and a level of 3o ppm of P is desired for top y.eWs of most crops, Strong Bray (P.)-This method determines the artourtof readily availablephospffcrus plus a part of the active reserve phosphorus in the soil. A 'anal of at least 40 ppm of P and preferably 60 ppm of'P or more is desired for good yields of most crops. SODIUM BICARBONATE (P) - This method determines tno amount of readily available phosphorus in calcareous soils (baying free lime present). A level Diet least 10 ppm of P and preferably 15 ppm of P or more is desired for good yields of most crops. For additional information+, of phosphorus availability and recommendation guides, see pages 13-21 in our book, "Sol: and Plant Analysls.' CATION EXCHANGE CAPACITY (CEC) The cation exchange capacity (C.E.C.) is a measure of the capacity of a soil to hold exchangeable cations. These include Hydrogen (H+), Calcium (Ca++), Magnesium (Mg++), Potassium (K-,) and Sodlunt (Na-:)- C.E.C. is measured in terms of ,niliiequ;valents (ineq.) per 100 grams of soil. it depends largely on the amount and type of clay present acid the organic matter content. The larger this valise, the more cations the sell is able to hold against leaching. ' PERCENT BASE SATURATION The balance for the soil colloid recommended by mast soil scientists is 65 to 75 percent calcium, 10 to 15. Percent magnesium, and from 2 to 5 percent potassium.. The percent base saturation is calculated trout the C.E.C. and percent saturation of Ca, Mg, K, H, and Na is reported to assist you in determining thebalance of cations in your soil. For additional Information and recommendation guide, see pages 25-29 in our book; "Soil and Plant Analysis:' pH Soil pH: The soil pH is measured on a 1:1 soil to water solution. The soil pH measures the active soil acidity to alkalinity. Mineral soits should have a pH of 6.0 to 7.0 for most crops, while a pH range of 5.0 to 5.5 is adequate for high orgartcsails. Buffer Index: The buffer fill is determined with the Shoemaker, McLean, and Pratt (SMP) buffer solution. The lime requirerreni is:determined by the depression m the buffer pH by acidity in the sot: sample. The arnount if ii_mestone reededto neutraiiza the acidity present lags already been Bete mined and the following table is a general guide; but variations from Diller published guides may occur due to differences in limestone fineness, neutralizing value, and plow deptl SALT pH: In areas ,where the SMP buffer is not used, a salt pH is determined. The salt pH of in soils is measured by adding 0.01 molar calcium chloride to the soil's solution. Soils which are highly leached and sandy soils may have a salt pH value as much as one whole unit lower than the soil pH, (i,e. 6.0- 5.0). The soil p i value of soils of average salt content may be lowered from 0.4 to 0.6 units by casing the calcium chloride. Depressions of the soil pH amounting to 0.1 units and lass upon the addition of calcium chloride occurs whon soils are exceedingly high in their content of salts. For additional Information or, soil pH arid liming guide, see pages 30-33 in our book, "Soil and Plant Analysis." LIME REQUIREMENT - TonsiAcre Limestone Mineral.Soils : Organic Soils Buffer Plow Depth Plow €Depth, Plow Depth Plow Depth : pH 6i•a inches = 9 inches 6„ inches 9 inches 7A none' none 0 0 6.9 none none 0 0 •i6.8 1 1.5 0 0 56.7 1,5 2 0 0 - 6.6 2 3 4:30 0 6.5 2.5 4 0 0 6A 3 4,5 1 1,5 6.3 3.5 5 2 3 _ c 6.2 a 4 6 2:5 3.5 &1 4,5 7 3 4,5 6,0 5.5 8 4 6 _ 5.9 6 9 4.5 6.5 _ . 5.8 •• 6.5 10 5 T5 5.7 7 11 5.5 8 5.6 8 12 6 9 5.5 9 13 6.5 10 lithe soil pH is above 6.5, no buffer index will be determined since lime would not be needed for most crops. Cropsuaised on organic soils (sails containing 20 or more organic matter) usually do not benefit from liming unless the soil pH is less than 5.3. ADJUSTMENTS FOR TYPE OF LIMING MATERIAL Two primary factors affect the actual amount of a given liming material required to achieve the desirable effect on soil pH. The total Nutrilizing Power (TNP, also referred to as Calcium Carbonate Equivalent) and the fineness of the timing material are these factors. The following table will serve as a gklde to miake these adjustments. Ag Ag A9 Ag Ag Super- Pulverized Ag Fine Course Granulate Hydrated fine Base Ground Meal Meal Slag Lbs. to equal 1 ton of 1-restone_ 11 GO 1900 2000 2300 2900 3400 2700 TNP 140-160 90+ 90+ 9tj+ 90- 90+ 90+ F f P N A 100 MESH f 00 8o 60% 40 30 20 5 E S 60 MESH 100 95 70! 50 40 30 15 N S 20 MESH 100 100 95°1 .70 60 50 50 E ,I S N S G - If ,the TNP is less than 90, multiply amount from above by these percen es: TNP 80-89 115 70-79 130 - , 60-69 150 LIMING: Apply lime only after the soil has been tested. Too much lime can be as harmful as too little. Lime must be thoroughly mixed with the soil for maximum effectiveness. If -both magnesium and calcium are needed, apply dolomite lime to help supply magnesium. EXCESS LIME: A visual rating of free lime present. Soils having high amounts of free lime available will have associated problems in the availability of major and. minor elements and difference In choice or amount of soil amendments. SOLUBLE SALTS: For infor;nation, refer to page 61 of our book, "Soil and Plan, Analysis." SULFUR: All crops need sulfur. The higher the nitrogen uptake by a crop, the greater the need for sulfur, A level of 15,20 ppmbf available sulfur should be maintained for most crops. For additional information on availability of sulfur and milking recommendations: see pages 22-24 in our book, "Soil and Plant Analysis." MICRONUTRIENTS The available levels of micronutrients are rated from very love to ve y high. However, applying the recommended amount of a certain minor element with a low`�ating will not necessarily insure a crop response because of the many factors which may influence micronutrlent response. Some of the factors whli;h influence response are: rapidly changing soil pH; excessive applications of N-P-K, sot: physical problems, soil moisture extremes, excessive leaching, crop variety, and plantpopulation. For additional information on why plants need micron6trients, their avallabi ity, interactions with other nutrients and a recommendation guide, see pages 34-45 in our book, "Soil and. Plant Analysis.' M "Our records and letters are for the exclusive and confidential use of our clients and may not be reproduced in whole or in part, nor may any reference be made to the work, the results or the company in any.advertising; news release, or other public announcements without obtaining our prior written authorization,' Copyright 1977 REPORT NUMBER: R215-036 ADDITION RN AGRICULTURAL LABORATORIES, INC. Dine Road • Richmond, Virginia 23237 • (804) 743-9401 Fax No. (804) 271-6446 SEND TO: 1= T n (_RO DIVISION PINF1 11_1_..F_ VIC ;'81'34-f_i388 DATE OF REPORT (_)e, f r ? 7 r' i' PAGE 1 SAMPLES GROWER: RC)L-;r_R'r L. i`lrf)RSH()LI_ SUBMITTED BY: SOIL ANALYSIS REPORT 0 COPY 'TO: DATA. RECEIVED VED ;:?i/i_? L .'�-c> D(1TE OF if) NALYSI'3 SAMPLE (DENT. LAB NO. Nitrogen N mg/kg Phos- phorus P mg/kg Potassium K mg/kg Sulfur S mg/kg Calcium Ca mg/kg Magnesium Mg mg/kg Sodium Na mg/kg Iron Fe mg/kg Aluminum Al mg/kg Manganese Mn mg/kg Copper Cu m09 Zinc Zn mg/kg Ammonia Nitrogen mg/kg Nitrate Nitrogen mg/kg J P-01 !L 9 LAB Cadmium Chromium Nickel Lead Arsenic Mercury Selenium Organic Total NO. Cd Cr Ni Pb As Hg Se Nitrogen pH C.E.C. i'1O mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg (meg/100g) 2055.7 1 r'?6 6 12 3. 33 0. 1 S O. 29 , 20558 1 26 7 19 3.47 0. 14 0.34 5 20559 1 57 12 21 4.04 C). 13 0.5C) 5 Our reports and letters are for the exclusive and confidential use of our clients, and may not be reproduced in whole or in part, nor may any reference be made This report applies only to the sample(s) tested. Samples are to the work, the results, or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization. retained a maximLLT, of t", .14y6i,after te,%ing:;l=-IS A&L EASTERN AGRICULTURAL LABORATORIES, INC. 1 REPORT NUMBER A&L EASTERN AGRICULTURAL LABORATORIES, INC. H215-087 7621 Whitepine Road • Richmond, Virginia 23237 • (804) 743-9401 Fax No. (804) 271-6446 -At ACC"T # 45469 SAMPLES SEND its . SRO DIVISION DON L D PAYN - ALS SUBMITTED ROSER't HAMILTO TO: GROWER: BY: COPY ' T0: ANNs4P�E LISs MD FOB 388 INEVILLE . NC 28134-038 DATE RECEIVES 08601�� DATE OF REPORT # � PAGE SOIL ANALYSIS REPORT BATE OF ANALYSIS 08 /02196 ° ORGANIC ",PHOSPHORUS POTASSIUM MAGNESIUM 'CALCIUM CI` . "SODIUM PH Cation ° 'PERCENT SAMPLE LAB MATTER � � P1 (Weak Bray) P2 : (Strom Bray) K M 9" Ca Na SOIL' "• BUFFER Hy DRO- GEN Exc hange Ca aci y P BASE SATURATION (COMPUTED) NUMBER NUMBER a�° , . ENA ° ._+ ,,«.. k ..... y*t ." H C.E.C. f M o� RATE: Ibs./A Ppm-P RATE ., ppm-P"RATE ° ppm K RATE "ppm-Mg RATE ATE PPm CaR ppm Na RATE' pH pH " ° meq/1 OOg "meq/1 OOg ' K 9 Ca H, Na 1 20560 9.8.14OV 154 VW24 0 230 V 320 VH 200 H 6.3 6.8' 1.1 10.3 5.7 25.8 2 20561,8.2 140V 1 44 V H :1 6 4 Vil 300 V 330 VH 990 M 6.4 6.9 0.81 8.8 8.7 31.2 51.1 . H. 9 3 0562.7. 3 140V . 60 V H , 88, V` 24C, V ' 310 VH G00 N 6.8 0.2 8.4 7.3 30.6 59.21. : 2. 9 4 056 3 ,, 4.5 13211 1 00 W'H -111 , V 14C V'S 150 VH ` 5 0 M 5.8 6. ` 1.11. 5.6 6.4 22.4 52.1119.0 5 056 .3.4 111H 139 Vm-:160 vv 12C V11 140 VH 550 R 6.1 6.9, 0.7 4.9 6.3 23.8 56.2 3..7 (SEE EXPLANATION ON BACK) n-' NITRATE SULS UR ZINC MANGANE$ E ° IRON IRON • COPPER BORON EXC ESS ' . 50LUBLE ' CHLORIDE MOLYB-: DENUM PARTICAL SIZE ANALYSIS , AMPLE Mn Cu B ; LIME " SALTS. CI Mo . �NUMBER m-No N, PP a- . , RATE ppm-Mo '/. % %o SOIL " RATE p m S RATE p . PP m-Zn RATE, -Mnm•Mn RATE P.pPm-Fe RATE ppm-Cu RATE .B RATE : a mmhos%m RATE PP m-CI RATE, RATE SAND SILT .CLAY TEXTURE 1 - 11 ' M 20. 6 VE 149 H 55 Vi 9.+6 V. .°1.2 M 2 11H16.7VH 33 H 4 6 H 3.6 V4 1.6M 3 11 -M 10.1 VH 32 H 15 H 4.2 V C 1.1 This report appli to the samples) tested. Samples are retained a 4 1 i _ 5. 3 H aC 19 H 4.9 V. 0<.7 N1 maximum oft ' days after testing. Soil Analysis prepared by: A A ER RICULTURAL L ORATOR S, INC. 5 11.4 5. H .18. M . 20 H 6..5 V 410.7 by r �vvv tv�), �vvv tt.), IVICuIVIVI kivl), Whin tn), VCnT Mum kvm), ANu IVUNC tIV). --'- NIULI IHLY I Ht HCJUL I IN ppm CY 4.b IU UUNVtH I I LtiS. VEX AUHt 1-2 5 v � ENR - ESTIMATED NITROGEN RELEASE ""' MULTIPLY THE RESULTS IN ppm BY 2.4 TO CONVERT TO LBS. PER ACRE K20 EXPLANATION OF SOIL ANALYSIS REPORT % ORGANIC MATTER AND ESTIMATED NITROGEN RELEASE (ENR) The % Organic Matter content is determined chemically cn the dried screened soil sample. However, the total organic content may be sornawhat h. her than reported because larger pieces of plant and animal residues are screened out prior to analysis. Only a part of the total nitrogen in the organic matter of a soil will become available for plant use during the growing season. Many factors such as: soft fnoisture, sail temperature. the soil's physical condition, and the arr,ount and. ype of crop residues present al' have an effect on bacterial action. Therefore the ENR value is only a guide to the nitrogen supp;y available for the growing crop. For additional information on r tregon ra:ease and recommendation guides, see pages 5-12 in our boot; "Sri[ and Plant Analysis.' Results:Theresultsforthemajorand minor plantfoodelements are reported npartsperx iiNon(ppnt) on an elemental basis. Conversions: T6 convert to lbs/A, the type of soil and tillage depth should be considered. Most mineral soils weigh approximately 2 million pounds (dry weigh) for an acre of soi. 61�4 to i inches deep, An arse of soil 10 inches deep woighs approximately 3 million pounds. In the past, most laboratories that reported results in lbs. per acre were considering 2 million ibs. of soil per acre (results in pprt x 2 lbs. per acre). However, with deeper tillage practices used today many ,rowers are dealing with nearly 3 miilion,bs. of soil per acre. CONVERSION TABLE Results n ppm 2 Mfl;on Ids. of soil per acre 6, 7 in. deep Hesults in Porn 3 Million lbs. of soil per acre n 9-10 in. d2op P x 2 = lbs. per acre of P P x 3 'bs. per acre'of P x 4.6 =. lbs. per acre of P205 x &9 =. ibs, per acre of P20s K x 2 lbs. per acre of K K x 3 - bs. per acre of K x 2.41 = ibs, per acre of KZO x 3.6 us. per acre of Kr0 Mg x 2 = lbs. per acre of Mig Mg x 3 bs. per acre a-' Pig Ca x 2 = lbs. per acre of Ca Ca x 3 ibs, per acre of Ca S x 2 - los, per acre of S S x 3 - 'bs. per acre of S S x 6 = lbs. per acre of SO4 S x 9 - bs. per acre of SO4 B, Zn, Mn, B. Zn. I - An, Fc, Cu. Palo Fe, Cu, Me x 2 = tbs. per acre of B, .... x 3 - lbs. per acre-o`' B, Zn. Mn, Fe, Cu, Me Zn, Nlm Fe, Cu. Mo PHOSPHORUS Two different tests are made and reported for availability of phosphorus in the soil sample. Weak Bray (P)-This method determines the amount of readily available phosphorus in the soil, A level of at ieast 20 ppm of P is desired for average crop production and a level of 30 ppm of P is desired for top yields of most crops. Strong Bray (P2) -This method determines the amount of readily available phosp' on;s plus a part of the active reserve phosphorus in the soil. A'evel of at least e.o ppm of P and preferably 60 ppm of P or more is desired for good yields of most crops. SODIUM BICARBONATE (P) -This method determines theamountof readily available phosphorus in calcareous soils (having free Ime present), A level of at least 10 ppm of P and preferably 15 ppm of P or more is desired for good yields of most crops. For - additional information of. phosphorus ava!!ability and recommendation guides, see pages 13-21 in our book, "Sol: and Plant Analysis." CATION EXCHANGE CAPACITY (CEC) : The cation exchange capacity (C.E.C.) is a measure of the capacity of a soil to hold exchangeable cations. These include Hydrogen (H+), Ca'c:um (Ca ++); Magnesium (Mg+i-), Potassium 1K-r) and Sodium (Na.). - C.E.C. is measured in terms of milliequivalents €tneq,) per i 00 grams of soil. !t depends largely on the amount and type pf day present and the organic matter content. The larger this vei:ue, thl more cations the soi' is able to he'd against leaching. PERCENT BASE SATURATION The balance for the soil co€':old recorrinnended by [nest soil sic enlis€s is 65 to 75 percent calcium. 10 to 15 percent magnesium, and from 2 to 5 percent potassium. The percent base saturation is calculated front the C,E,C. and percent smuraton of Ca, Mg, K, H, and Na is reported to assist you in determining the balance of cations in your soil. For additional information and recommendation guide, see pages 25-29 in our book. "Sol: and Plant Analysis.' 3L Soil PH: The soil pH is measured on a'1:1 soil to water solution. The soil pH measures the aceive soil acidity to:a'kalinity: Mineral sells should have a pH of 6.0 to 7.0 for most crops, while a pH range of 5.0 to 5.5 is adequate for high organic soils. Buffer Index: The buffer pH is determined with the Shoemaker, McLean, and Pratt (SMPi buffer solution. The lime re,uiremant is.determined by the depression of the buffer pH by acidity in the coil sample, The a mount if limestone needed to neutralize the acidity present has already been determined and the following table is a general guide; but variations from other published guides may occur due to differences in limestone fineness, neutralizing value, and p€ow depth. SALT pit: In areas w*ere the SMP buffer is not used, a salt pH is determined. Tile salt pH of th sof's-is measured by adding 0 01 molar calcium chloride to the soil`s soiu ion So is which are highly leaded LIME REQUIREMENT Buffer pH Tons Acre Limestone Mineral Soils -' Flow Depth Plow Depth 6 11 inches 9 inches 0manic Soils Plov Depth Plmv Depth u%s inches 9 inches -- TO nos none 0 of 6.9 none none 0 0 2 .0 0 _ 6.6 2 3 0 6.5 2.5 4 0 0 6A 3 4,5 1 1.5 .6.3 3.5 5 2 3 „ _6.2 ., 4 6 .. _ 2.5 3.5 .. 6.1 4.5 _ 7 3 4.5 6.0 5.5 8 -• 4 6 5.9 6 9 6.5 5.8 5.5 10 5v T5 __ 5.7 3 5.5 8 5.61 H ?2 6 9 5.5 9 .., 6.5 10 If the soil pH is above 6.5, no buffer index vviil be determined since lime would not be, nestled for most crops. Crops raised or; organic soils (soils containing 20% or more organic matter) usually do not benefit frorn liming un':.ess the soil pH is less than 5.3. ADJUSTMENTS FOR TYPE OF LRAING MATERIAL Two primary factors affect the actual amount of a c,?van liming material required to achieve the desirable effect on soil pK The iota! Nutrlizing Power (TNP, also referred to as Ca:cirnr Carbonate Equivalent) and the fineness of the imina material are ti;ese factors. The fcl owing table will se..,ve as a gull -a to make these adj.ustrnerl Ag Ag Ag Ag Ag Super- Pulverized Ag Fins Course Granulate Hydrated fine Base Ground ;Neal Meal Slag Lbs. to equal ? ton of Lim estone 1100 1900 2000 2300 2900 3400 2700 TNP 140-160 90+ 90+ 90+ 90-r 90+ 90+ F I N A 00 MESH '00 80 60% 40 30 20 5 E S 60MESH 1;00 95 70! 50 40 30 35 N S 20 MESH ? 00 1.00 95 %c 70 60 50 50 E I S N S G if the TNP is less than 90, multiply amount from above by these percentages: TNP 80-89 115 70-79 130 60-69 150 Apply lime only after the soil has been tested. Too much lime can be as harmful as too little. Lime mustbe thoroughly mixed with the soil for maximum effectiveness. If both magnesium and calcium are needed, apply dolomite lime to help suppy magnesium. EXCESS LIME: A visuat rating of free lire present. Soils having high amounts of free lime available will have associated problems in the availability of major and manor elements and difference in choice cr amount of soil amend,rents. SOLUBLE SALTS For information: refer to page 61 of our book, "Soil and Plant Analysis." SULFUR: All crops need sulfur. Tile higher the nitrogen uptake by a crop, the greater the need for sulfur. A level of 15-20 ppm of available sulfur should be maintained for most crops. For additionat information on availability of sulfur and making recommendations. see pages 22-2? in our book. "Selland Plant Analysis." MICRONUTRIENTS The available levels of micionutnents are rated from very low to very high. However, applying the recormnended amount of a certain minor element with a tow rating will not necessarily insure a crop respor se because of he many factors which`. may influence micronurrient response. Some of the factors which influence response are: rapidly changing soil pH, excessive applications of N-P K, soilphysical problems, soil moisture extremes, excess!: e leaching, crop variety. pod part population. For additional nformation on why plants need micienutrients, their ava?lab i`y; interactions :vith other nutrients and a eco ime, dation guide, see pages 34.45 in our book. "Soil and Plant Analysis." and sandy soils may have a sat:' pH value as much as one r hole unit lower than the soil pH. (Le, 6.0- 5.0). The soil PH value of soils of average salt content may be lowered from 0.4 to 0.6 units by using I! re calcium chloride. Depressions of the soil pH amounting to 0.1 units and less upon the addinen of calcium chloride occurs v;hen soils are exceedingly high :if their content of sails. For additional information or'.soil pH and timing guide, see pages 30-33 n our cook, 'Soli and Plant Analysis." "Our records and letters are for tite exclusive and confidential use of our clients and may not be reproduced in whole or in part, nor may any reference be made to the work, the results or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization." Copyright 1977 0 i REPORT NUMBER A&L EASTERN AGRICULTURAL LABORATORIES, INC. R215 -087 7621 Whitepine Road • Richmond, Virginia 23237 • (804) 743-9401 Fax No. (804) 271-6446 Met SEND SIC GRO DIVISION TO: POE 388 PINEVILLE NC . 28134-0388 DATE OF REPORT 08105/96 PAGE 2- GROWER: iiONALD PAYNE - AL5 SOIL ANALYSIS REPORT ACCT # 45469 SAMPLES SUBMITTED ROBERT HAMILTON BY: COPY TO:. ANNAfPOLISr MD RECEIVED 08/01I96 DATE OF ANALYSIS 08/02196 ORGANIC PHOSPHORUS POTASSIUM. MAGNESIUM CALCIUM SODIUM pH Cation PERCENT SAMPLE LAB MATTER* HYDRO- Exchange BASE SATURATION (COMPUTED) Pi K M Ca Na SOIL BUFFER NUMBER ;NUMBER9 o { Weak Bra y) (Strong?Bray) M x w GEN H ' Capacity C.E.C. o �O' 0 /o 0 / 0 H 0 /o % , ENR RATE lbs./A' *+ m,P RATE pp - .... pP m-P RATE ppm-K RAT E ppm-Mg ppm-Ca ppm-Na RATE' pH pH rneq/100g meq/100g. K Mg Ca H Na b 2056 5 : 3.3.1091q 130 VH-145',Vf 11 C Vil 120 VH 540 M 5.9 6.9 0.8 +.8 5.9 0.8 56.2 7.1 7 20566.3.1 105M 142 VH I E 9 VE 100 H 120 VH 520 M 5.9 6. 9 , 0.8 4.7 5.5 21.5 55.9 7.1 t 0567.6■ 0. 140V 60 VH W-0 18C V 210 - Vfl 780 M 6.0 6.8 � 1.1 7.2 6.4 4.2 54.0 5.4 9 20568 . 6.1 140V ` 69 V H . 78 VH 191D V11 220 VH 800 M 5.9 6.8 1.3 7.6 6.4 24.0 2.4 7.1 10 20569.4.7 1.34H dig V H , 77'VV 17C VDI 200 VH 730 bM 5.7 6.8 1.5 7.3 6.0 22.9 0.1 1.1 (SEE EXPLANATION ON BACK) SAMPLE NUMBER NITRATE NO3 m•N3' N PP a RATE. SULFUR S ppm..-S RATE ZINC Zn PP m-Zn RATE MANGANESE Mn ppm-Mn RATE IRON Fe ppm-Fe RATE COPPER Cu ppm-Cu RATE BORON B ppm-B RATE EXCESS LIME RATE SOLUBLE SALTS mmhos/cm RATE CHLORIDE CI ppm-CI RATE pp MOLYB- DENUM Mo. Pp m M o- RATE PARTICAL SIZE ANALYSIS . SAND AND IL SILT CLAY SOIL TEXTURE .' 6 11 'M 5. 5 H 17 P1 18 H 5.7 V :0.7 M 7 11 ,M 6. 7 H 1S IN 22 7.2 V4,046 M 8 11 ,M - 9. 7 VH 3S H 21 ,H 3.0 f$ ... 0.8 M Thisae sample(s) tested. Samples are retained a 9 11 NM 8. 6 Vti 37 H 22 H 2.8 H , 0.9 M maxiter testing. Soil Analysis prepared by: ICULTURAL LA ATORI , INC. 1 0 11 7. 61 .2 5, Hl 18 W 2.1 : H 1.1 b CODE TO RATING: VERY LOW (VL), LOW (L), MEDIUM (M), HIGH (H), VERY HIGH (VH), AND NONE (N). -"' MULTIPLY THE RESULTS IN ppm BY 4.6 TO CONVERT TO LBS. PER ACRE P205 // ' ENR - ESTIMATED NITROGEN RELEASE ""' MULTIPLY THE RESULTS IN ppm BY 2.4 TO CONVERT TO LBS. PER ACRE K20 11 EXPLANATION OF SOIL ANALYSIS REPORT ORGANIC MATTER AND ESTIMATED NITROGEN RELEASE (ENR) " The % Organic Matter content is determined chemically on the dried screened soil sample-. However, the total crganic content may be somewhat higher than reported because larger nieces of plant and anima: residues are screened out prior to analysis. Only a part of the total nitrogen in the organic m3ner.6f a soil will become available for plant use during the growing season. Many factors such as: sail moisture, soil temperature. the soil's physical eordition, and the amount and type of crop residues presonl al': have an effect on bacteral action. Therefore the ENR value is only a guide to the nitrogen supply available for the growing crop. For additional information on nitrogen.release and recommendation guides, see pages 5-12 it our book "Sell and Plant Analysis." Results: The rresultsforthe major and minor plant food elements a-ereported in parts per million (ppm) or. an elerner tan basis. Conversions: To convert to Ibs; A, tite type of soil and tillage depth should be considered. Most mineral soils weigh approxirro rely 2 miliion pounds (dry weight) for an acre of soil 61%. to 7 inches deep, An acre of soil i0 inches deep weighs approximately 3 million pounds. In tite past, most laboratories that reported results in lbs. per acre were considerng 2 million lbs. of soil per acre (results in pprn x2 .r Its. per a ro). However, with deeper tillage practices used today many growers are dealing with nearly 3 million lbs. of soil por acre. CONVERSION TABLE 2 Million lbs. 3 Million Ibs. Results of soil per acre Results of soil per acre in Dpm 6'h-7 in. deep in porn in 9-10 in. deep P x 2 = lbs, per acre of P P x 3 Ibs. per acre"of P x 4.6 = lbs. per acre of P20s x 6.9 lbs. per acre of P 05 K x 2 = ins. per acre of K K k 3 = Ibs. per acre of K x 2.4 = Ibs, per acre of K,O x 3.6 = lbs. per acre a Kz0 Mg x 2 lbs. per acre of Mg Mg x 3 lbs. per acre of Mg Ca x 2 = los, per acre of Ca Ca x 3 = bs. per acre of Ca S x 2 = lbs, per acre of S S x 3 = lbs. per acre of S S x 6 = Ibs, per acre of SO4 S x 9 = lbs. per acre cf SO4 B, Zn, Mir, B, Zn, Mn, Fe, Go, Me Fe, Cu, trio x 2 = loos. per acre of B, x 3 = ihs. per acre of B, Zn, Mn. Fe, Cu, Me Zn, Mn, Fe, Cu. Me PHOSPHORUS Two different tests are made and reported for availability of phosphorus in the loll sample. Weak Bray (Pr) -This method determines the amount of readily available phosphorus in the soil. A revel of at least 20 ppm of P is desired for averace crop production and a level of 30 ppm of P is desired for top yields of most crops. Strong Bray (P2) - This method determines the amount of readily available phosphorus plus a part of the active reserve phosphorus in the soil- A level of at least 40 ppm of P and preferably 60 pom of P or more is desired for good yields of most crops. SODIUMBICARBONATE (P)Thsmethoddeterminesmeamountofreadilyavailable phosphorus in calcareous soils (having free lime present}. A level of at least 'to ppm of P and pretarabiy 15 ppm of P or more is desired for good yields of most crops. For additional information of phosphorus availability and recommendation guides, see pages 13-21 in our book. 'Soil and Plant Analysis.' CATION EXCHANGE.CAPACITY (CEC) The cation exchange capacity (C.E.C.) is a measure of the capacity of a soil to hold exchangeable cations. These include Hydrogen (H+), Calcium (Cat_i), Magnesium (Mg 4-.), Potassium (K+) and Sodium (No ), C.E.C. is measured in terms of mi8iequivalents (meq.) per 100 grams of soil. It depends largely on the amount and type of clay present and the crganic matter content. The larger this valrie, the more cations the soil is able to hold against leaching. PERCENT BASE SATURATION The balance for ;fie soil colloid recommended by most soil scientists is 65 to 75 percent calcium, 10 to 15 percent magnesium, and front 2 to 5 percent potassium. The percent base saturation is calculated from the C.E.C. and percent saturation of Ca, Mg, K, H, and No is reported to assist you in determining the balance of cations in your soil. For additional information and recommendation guide, see pages 25-29 in our book, "Soil and Plant Analysis." pH Soil pH: -1lie soil pH is measured on a 1:1 soil to water solution.'! he soil pH measures the aciive soil acidity to atka?i.nify Mineral soils should have_a pH of 6.0 to 7.0 for most crops, while a pH range of 5.0 to 5.5 is adequate for high organic sails. LIME REQUIREMENT Buffer -pH Tons/Acre Limestone Mineral Soils Picvr Depth Plow Depth 61,,,inches 9inches Organic Soils Plow Depth Plow Depth 6%,inches_ 9incnes 7.0 noina none 0 0 6.9 none none 0 0 6.8 1 1.5 0 0 - e6.7 1.5 2 - • ..0 0 6.6 2 3 0 0 6.5 2.5 4 0 0 6.4 3 4.5 1 1.5 6.3 3.5 -_ 5 - 2 3 - 6.2 4 6 2.5 3.5 6,1 4.5 7 3 4.5 6.0 5,5 8 4 6 5.9 6 9 <=.5 6.5 5.8 6.5 i 0 5 7.5 5.6 8 12 6 9 5.5 9 13 6.5 10 little soil pH is above 6.5, no buffer index will be determined since lime would not be needed for most crops. Crops -raised on organic soils (soils containing 201% or more organic matter) usually do not benefit from liming unless the soil pf i is less than 5.3. ADJUSTMENTS FOR TYPE OF LIMING MATERIAL Two primary factors affect the actual amount of a given liming material required to achieve the desirable effect on soil pH. The total Nutrilizing Power (TNP, also referred to as Calcium Carbonate Equivalent) and tine tinenesss of the liming material are those factors. The following table will serve as a gyide to make these adiustrrents. Ag Ag Ag Aa Ag Super- Pulverized Ag Fine Course Granulate Hydrated fine Base Ground Meal Meal Slag Lbs.to equal 1 ton of Limestone 1100 1900 2000 2300 2900 3400 2700 TNP 140-i60 90+ 90+ 90+ 90+ 90+ 90+ F % P I N A 100 MESH 100 80 60% 40 30 20 5 E S 60 MESH 100 95 704% 50. 40 30 15 N S 20 MESH 100 100 95% 70 60 50 50 E [ S N S G If the TNP is less than 90, multiply amount from above by :hose percentages TNP 80-69 i 15 70-79 130 60-69 150 LIMING: Apply lime only after the sail has been tested. Too much lime can be as harmful as toe little. Lime musrbe thoroughly mixed with the soil for maximum effectiveness. If both magnesium and caiciarn are needed, apply dolomite lime to help supply magnesium. EXCESS LIME: A visual rating of 'free lime present. Soils having high amounts of free lime available will have associated problems in tine availability of major and minor elements and difference in choice or amount of soil amendments. SOLUBLE SALTS: For information, refer to page 61 of our book, "Soil and Plant Analysis." SULFUR: All crops need sulfur. Tl1e higher the nitrogen uptake by a crop, the greater the need for sulfur. A level of 15-20 ppm of evailabie sulfur should be maintained for most crops. For additional information, on availability of su [fur and making recommendations, seepages 22-24 in our book, "Soil and Plant Ana.sis." Buffer Index: The buffer pH is determined with tite Shoemaker, McLean„ and Pratt (SMP) buffer MICRONUTRIENTS solution. The lime requirement is detenmined by the depression of €ne buffer pH by acidity in tire soil sample. The amountlflimestoneneeded toneutralizetheacidity po senthasalreadybeendetermined Tte available levels of micronuirierts'are rated from very low to very high. However, applying the and the following table is a general guide, but variations from other published guides may occur due recommended amount of a certain minor element with a low rating will net necessarily insure a crop to differences in limestone, fineness. reuiralizing value, and plow dept;y. esDonsts because of the many factors which may influence micronutrient response. Some of the factors whiE'n influence response are: rapidly changing soil pH, excessive applications of N-P-K, so!. physical SALT pH: problems, soil moisture extremes, excessive leaching, crop variety. and plant population. For additional information on why plants need rnicronurients, their availability, interactions with other nutrients and a In areas where the SMP buffer is not used. a salt pH is determined. The Bait pH bf in soils is recommendation guide, see pages 34-45 in our bock. "Soil and Plant Analysis." measured by adding 0.01 molar calcium chloride to the sail's sciution. Sans which are highly leached and sandy soils may have a salt pH valise as much as one whc'e unit louder than the soil pH, ti,e. 6.0- 5.0). The soil pH value of soils of average salt content may be lowered horn 0.4 to 0.6 units by using - .. the calcium chloride. Depressions of the son' pH arriounting to 0.1 traits and less upon the addition of calcium chloride occurs when soils are exceedingly high in their content of salts. For additional information on soil p!-1 and liming guide, see pages 30-33 in our book, "Soil and Plant Analysis:' "Our records and letters are for the exclusive and confidential use of our clients and may not be reproduced in whole or in part, nor may any reference be made to the work, the results or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization." Copyright 1977 REPORT NUMBER A&L EASTERN AGRICULTURAL LABORATORIES, INC. R215 °-087 7621 Whitepine Road • Richmond, Virginia 23237 • (804) 743-9401 Fax No. (804) 271-6446 MOMLA SEND EIO GRO DIVISION TO: PDB.388 PINEVILLE NC 28134-0388 DATE OF REPORT 08105I 96 PAGE 3 € ONALD PAYNE ' AL5 GROWER: SOIL ANALYSIS REPORT . ACCT # 45469 SAMPLES SUBMITTED ROSERT HAMILTON BY: COPY TO: ANNAPDLISo MD DATE' RECEIVED 08101 /96. DATE OF ANALYSIS 08102/96 ORGANIC PHOSPHORUS POTASSIUM MAGNESIUM CALCIUM SODIUM pH Cation PERCENT SAMPLE LAB MATTER HYDRO- Exchange BASE SATURATION (COMPUTED) Pi PS K Mg Ca Na SOIL BUFFER NUMBER, NUMBER ' *` (.Weak Bray) (Strong Bray) » » .: » GEN H Capacity C.E.C. ° o 1 ENR RATE lbs./A ... ppm-P RATE .»»» ppm-P RATE . .»»». ppm-K RATE- ».. ppm-Mg RATE ppm-Ca RATE *.» ppm-Na RATE pH' pH meq/1 OOg meq/100g K Mg Ca H Na 11 2057 0 : 7. 0 140V _ 71 V H , 90 VH 170 VA 220 VH 820 M 6.0 16..8 1.2 7.5 5.8 4.4 54.5 5.4 12 0571 ,, 6.0 140VO 60 V H . 73 VE 16C V11 210 VH 750 L 5.6 - 6.8- 1.8 7.7 5.3 2.7 : 48.7 23.3 13 20572;-4.3.128H 49 V'H - 55 H 14C V ' 170 VH 650 M 6.0 . 6.8 -0.9 5.9 6.0 23.3 54.7 - 5.4 14 057 3 _- 4.5 132V21 61 V H _ 83 V 14C V11 160 VH 620 M 5.9 . 6. 8 1.0. L5.8 6.2 Z3.1 53.6 7.1 15 20744 4.1 124H '; 68 V Irk 76 0 14C V11 150 VH 620 M 5.9 6.8 1..0 5.7 .6.3 22.0 4.5 , 7.1 (SEE EXPLANATION ON BACK) SAMPLE, NUMBER NITRATE , NIN033TE 3 -N RATE SULFUR $ S ppm-S RATE ZINC Zn.. ppm-Zn RATE MANGANESE Mn ppm-Mn RATE IRON Fe ppm-Fe RATE COPPER Cu ppm-Cu RATE BORON B ppm-B RATE EXCESS LIME RATE SOLUBLE SALTS mmhoslcm RATE CHLORIDE Cl ppm-CI RATE MOLYB- DENUM Mo ". ppm-Mo RATE PARTICAL SIZE ANALYSIS % SAND % SILT % CLAY SOIL TEXTURE 11 11:4 8.9.VH °3e H 23 H- 2.8 H .0.9 M 12 11,N :"7,6 H :27 H 17 H 1..9 H 0.8 fq 13 11 .M 4.1 H I N 12 H 1.4 H ,0.7 'M This report ies to the sample(s) tested. Samples are retained a 14 4 i 1 14 5. 0 H �I i 7 ML 1 4 H y !• 5 H 07M maximum irty da s after testing. Soil Analysis prepared by: & L E TER GRICULTURAL BORATORI S, INC. 15 11 P+� .4. 8 H It 15 H 1.5 H. 0.7 M C. NoA j _ by CODE TO RATING: VERY LOW (VL), LOW (L), MEDIUM (M), HIGH (H), VERY HIGH (VH), AND NONE (N). -"-- MULTIPLY T HE RESULTS IN ppm BY 4.6 TO CONVERT TO LBS. PER ACRE P205 / / ✓ ENR - ESTIMATED NITROGEN RELEASE ""' MULTIPLY THE RESULTS IN ppm BY 2.4 TO CONVERT TO LBS. PER ACRE K20 U EXPLANATION OF SOIL ANALYSIS REPORT % ORGANIC MATTER AND ESTIMATED NITROGEN RELEASE (ENR) The Organic Matter content is determined chemically on the dried screened soil sample. However, the total organic content may be somewhat higher than reported 'because larger pieces of plant and aninfi l residues are screened out prier to analysis. Only a part of the total nitrogen in the organic matter o` a soil wi l become available for plant use during the growing season. Many actors such as: soft moisture, soil temperature, the soil's physical condition, and the amount and type of crop residues present all have an effect on bacterial action. Therefore the ENR value is only a guide to the nitrogen supply available for the growing crop. For additional information on nitrogen release and recommendaliongu`des, see pages 5-12 in our beef; "Soil and Plant Analysis." Results: The results for the major and minor plant food elements are reported in parts per million (ppm) on an elemental basis. Conversions: Tocortvert to lbs/A. the type of soil and til!ace depth shculd be considered. Most mineral soils weigh approximately 2 million pounds (dry,,veight) for an acre of soil 6' i to 7Inches deep. An acre of soil 10 inches deep weighs approximately 3 million: pounds. Ir, the past, most laboratories that reported results in tbs. per acre. were considering 2 million tbs. of soil per acre (results, ir. ppm x 2 s lbs. per acre). However, with deeper tillage practices used today many growers are dealing with nearly 3 million ins. of soil per acre. CONVERSION. TABLE 2 {:4i➢ion lbs. 3 Mi'fion lbs. Results of soil per acre Results of soil per acre in ppm 61%'2-7 in. deep in ppm in 9-10 in. deep P x 2 = lbs. per acre of P P x 3 -- 'ins. per arse of P " x 4.6 = lbs. per acre of P205 x 6.9 = lbs. per acre ct P205 _ K x 2 = lbs. per acre of K K x 3 = lbs. per acre cf K x 2.4 = lbs. per acre of K20 x 3.6 = lbs. per acre of K20 Mg x 2 = inns, per acre of Mg Mg x 3 = lbs. per acre of I'Ag Ca x 2 = lbs, per acre of Ca Ca x 3 = lbs. per acre of Ca S x 2 = los. per acre of S S x 3 = lbs, per acre of S S x 6 = lbs. per acre of SO, S x 9 = lbs. per acre of SO4 B, Zn, Mn, B. Zn. Mr., Fe. Cu, Mo Fe, Go, Me x 2 - lbs. per acre of B, x 3 - lbs. per acre -of B, Zn. Mn. Fe. Go, Mc Zn, A4n. Fe, Go, Me PHOSPHORUS Two different tests are made and reporled for availability of phosphorus in the soil sample. Weak Bray (Pt) -This method determines the amount of readily available phosphorus in the soil. A level of at !east 20 ppm of P is desired for average crop production and a level of 30 ppm of P is desired for top yields of most crops. Strong Bray(P,)- This method determines the amountot readily available phosphorus plus a part of the active reserve phosphorus in the soil. A level of at least 40 ppm of P and preferably 60 ppm of P or more is desired for good yields of most crops. SODIUM BICARBONATE (P) - This method determines tF.e amount of readily available phosphorus in calcareous soils (having free lime present). A level of at least 10 ppm of P and preferably 15 ppm of P or more is desired for good yields of most crops.. For _ additional information of; phosphorus availability and recommendation guides, see pages 13-21 in our book. "Soli and Plant Analysis." CATION EXCHANGE. CAPACITY (CEC) The cation exchange capacity (C,E.C.) is a measure of the capacity of a soil to hold exchangeable cations. These include Hydrogen (H+), Calcium (Caa-+), Magnesium (Mg+i-), Potassium (K-) and Sodium (Nat). C.E.C. is measured in terms of milliequivalents (meq.) per 100 grams of soil. Itdepends largely or: the amount and type of clay present and the organic matter content. The larger this value, the more cations the soil is able to hold against leaching. PERCENT BASE SATURATION The balance for the soil colloid recommended by most soil scientists is 65 to 75 percent calcium. 10 to 15 percent magnesium, and from 2 to 5 percent potassium. The percent base saturation is calculated from the C.E.C. and percent safutabon of Ca, hag, K, H, and Na is reported to assist you in determining the balance of cations in your soil. For additional information and recommendation guide, see pages 25-29 in our book,'Soil and Plant Analysis." MIL Soft pH:'rhe soil pH is measured on a +.:I soil to :eater solution. The soil pH measures the active soil acidity to alkali^try. Mineral,soils should have a pH of 6.0 to 7.0 for most crops, whi'e a pH range of 5.0 to 5.5 is adequate for high organ'csoils. Buffer Index: The buffer pH is determined with the Shoemaker, f.1cl-ean, and Pratt (SMP) buffer solution. The lime requirement is determined by the depression al, the buffer pH by acidity In ilia soil sample. The amount if limestone needed to neutralize the acidity present has already been determined and the following table is a general guide; but variations from other published guides may occur due to differences in limestone fineness; neutralizing value, and plow depth. SALT pH: LIME REQUIREMENT Buffer pH Tons.'Acrs Limestone Mineral Sails Plow Depth Plow Depth 6Y- inches - - 9 inches , - Organic Soils Plow Dept, Ploy Depth 6%5 inches 9 inches TO none none 0 0 6.9 none none 0 0 6'.8 1 i .5 0 0 6.7 f,5 2 0 0 6.6 2 3 0 0 6.5 2.5 0 0 6A 3 - _ 4.5 1 1.5 (5.3 3.5 5 2 3 ..6.2 • 4 _ - 6 2.5 3.5 6.1 4.5 7 3 4.5 6.0 5.5 8 4 6 5.9 6 9 't.5 6.5 5.8 6.5 _ 10 5 7.5 5.7 7 15.5 a 5.6 8 12 6 9 5.5 9 13 6.5 to If the soil pH is above 5.5, no buffer index wit{ be determined since lime wculd not be needed for most • crops. Crops raised on organic soils (soils containing 20%or more organic matter) usually do not benefit from fiming unless the soil pH is less than. 5.3. ADJUSTMENTS FOR TYPE OF LIMING MATERIAL TWO primary factors affect the actual amount of a given liming material required to achieve the desirable effect on soi: pH. The total Nutrilizing Power (TNP, also referred to as Calcium Carbonate Equi alent) and the fineness of the liming materiai are these factors. The following table will serve as a guide to make these adjustments. Ag Ag Ag Ag Ag Super- Pulverized Ag Fine Course Granulate Hydrated fine Base Ground Meal Meal Slag Lbs. to equal 1 ton of Limestone 1100 1900 2000 2300 2900 3400 2700 TNP 140-160 90+ 90+ 90+ 90, 90+ 90+ F I P N A 100 MESH 100 80 601,•0 40 30 20 5 E S 60 MESH 100 95 70% 50 40 30 15 N S 20 MESH 100 100 95% 70 60 5o 50 E I S N S G If the TNP is less than 90. multiply amount from above by these percentages: TNP 80-89 115 70-79 130 60-69 i50 LIMING: Apply lime only after the soil has been tested. Too much lime can be as harmful as too tittle. Lirhe mustbe thoroughly mixed with the soil for maximum effectiveness. If both magnesium and calcium are needed, apply dolomite Lme to help supply magnesium. EXCESS LIME: A visual rating of free lime present. Soils having high amounts of free lime available will have associated problems in the availability of major and minor elements and difference in choice or amount of soil amendments. SOLUBLE SALTS: For information, refer to page 61 of our book, `Soil and Plant Analysis." SULFUR: All crops need sulfur. The higher the nitrogen uptake by a crop, the greater the need for sulfur. A level of 15-20 ppm of available sulfur should be mairts'ned for most crops. For additional information on availability of so [fur and making recommendations: seepages 22-24 in our book. "Soil and Plant Analysis." MiCRONUTRIENTS The available levels of micronutrionts are rated from very low to very high. However, applying the recommended arnount of a certain minor element with a low rating will not necessarily insure a crop esponse because of the many factors which may influence micronutrient response. Some of the factors which influence response are: rapidly changing soil pH, excessive applications of N-P-K, soil physical problems, soil moisture extremes, excessive leaching, crop variety, and plant population. For additional information on why plants reed micronutrienis, their availability, interactions with other nutrients and a In areas ,.-here the SMP buffer is not used. a salt pH is determined. The salt pH of th soils is recommendation guide. see pages 34-45 in our book. `Soil and Plait Analvsls.' measured by adding 0.01 metal, calcium chloride to the soil's solution. Soils which are highly leached and sandy soils may have a salt pH value as much as one whole unit lower than the soil pH. (i.e. 6.0- 5.0). The soil pH value of soils of average salt content may be lowered from 0.4 to 0.6 units by using the calcium chloride. Depressions of the soi: pH amounting to 0.1 units and less upon the addition of calcium chloride occurs when soils are exceedingly high .n their content of salts. For additional information on soil pit and liming guide, see pages 30.33 In our book, 'Soil and Plant Analysis." "Our records and 4etters are for the exclusive and confidential use of our clients and may not be reproduced In whole or in part, nor may any reference be made to the work, the results or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization." Copyright 1977 13 w � REPORT NUMBER R215-087 A&L EASTERN AGRICULTURAL LABORATORIES, INC. 7621 Whitepine Road • Richmond, Virginia 23237 • (804) 743-9401 LAI, Fax No. (804) 271-6446re t SEND BIO GRO DIVISION TO: POO 338 ILL.-2�134-0338 DATE OF REPORT 0 105/ 96 PAGE 4 DOA LD PAYNE - AL5 GROWER: SOIL ANALYSIS REPORT A CCT 45469 SAMPLES SUBMITTED ROBERT . HJAMILTON BY: COPY T0: ANNAPOLISr -ND DATE RECEIVED 08/DI/96 DATE OF ANALYSIS 08102/96 ORGANIC PHOSPHORUS POTASSIUM MAGNESIUM CALCIUM SODIUM - " pH1. „ Catiori PERCENT SAMPLE LAB %MATTER** HYDRO- GEN Exchan a Capacity P Y B SATURATION TIO U N BASE SATU (COMPUTED) ` P1 (Weak Bray) P2 ,(Strop Bray) K M' g Ca ° ,. Na SOIL BUFFER ° NUMBER NUMBER ENR «:. .._ :. H C.EC: o % /o % % RATE lbs. A ppm P RATE , ppm-P RATE ppm-K RATE",, ppm-Mg' RATE ppm-Ca RATE ppm-Na RATE" pH pH„ ' meq/100g meq/100g K Mg Ca H Na 16 0� 75=:,4.4 130V! 82 VH 42 V 1�40 V 150 V�H 590 6.0 6.9 0' 5.4 �i.� 3. 4m7 5.4 17 057 6 : 4. ► 132V 1 O6 V H _ 127 .01 15C Vill 150 ' VfH 610, M 6.1 6.9 0.7 5.4 7.1 23.0 56S2 13. 7 (SEE EXPLANATION ON BACK) SAMPLE NUMBER NITRATE No ppm•Nc N SULFUR S pp m S RATE ZINC .° Zn m Zn .. ° PP MANGANESE Mn ' ppm-Mn RATE • ° IRON ," Fe , ppm-fe' RATE COPPER , Cu ppm•Cu RATEgy, BORON B :' ppm•&RATE�g EXCESS LIME ' RATE • . SOLUBLE SALTS mmhos/cm RATE CHLORIDE Cl, Pp m-CI RATE � MOCYB- DENUM Ma pPm-Mo RATE P,ARTICAL SIZE -ANALYSIS % .' SAND % SILT S % CLAY SOIL ° ' [ 'TEXTURE , , y gp. �yRAT�,Eg ,q� }py 17 1.6 This report plies to the sample(s) tested. Samples are retained a makimu thin a after testing. Soil Analysi red by: A & L STE BICULTURAL L ORATOR[ S, INC. C. NORMA by V VUc I V RA I NU: VERY LUVV (VL), LUVV (L), MtUIUM (M), HIUH (H), VERY H1UH (VH), ANU NONE (N). .... MULI IDLY I HE HLbULIS IN ppm BY 4.6 1 U CONVERT TO LBS. PER ACRE P205 // 1 ENR - ESTIMATED NITROGEN RELEASE MULTIPLY THE RESULTS IN ppm BY 2.4 TO CONVERT TO LBS. PER ACRE K20 V \ EXPLANATION OF SOIL ANALYSIS REPORT % ORGASMIC MATTER AND ESTIMATED NITROGEN RELEASE (ENR) The % Organic Matter content is determined chemically on the dried screened soil sample. However, the total orga nic ccrtent may be samewhat higher than reported because larger pieces of plant and anlroa. residues are screened olA prior to analysis. Only a part of the total nitrogen in the organic matter of a soil will become available for plantuse during the growing season. Many factors such as: sail moisture, soil temperature. the soil's physical condition, and the amount and type of crop residues prese6i at'have an effect on bacterial action. Therefore the ENR value is only a guide to the nitrogen supply available for the growing crop. For additional information on nitrogen release and recommendation guides, see pages 5-12 in our boot; "Soil and Plant Analysis." Results: The results for the major and minor plant food elements are reported in parts per million ;ppm) on an elemental.basis. Conversions: To co. fVert"to Ibs.'A, the type of soil and tillage depth should be considered. Most mineral soils weigh approximately 2 million pounds (dry weight; for an acre of Sail 6 k to 7 inches deep. An acre of soil 10 inches deep weighs approximately 3 million pounds. In the past, most laboratories that reported results in lbs. Per acre were considering 2 million lbs. of soil per acre (results in pprn x 2 e lbs. per acre). However, with deeper tillage practices used today many growers are dealing with nearly 3 millionrlbs. of soil per acre. CONVERSION TABLE 2 Million lbs. 3 irli`llon lbs. Results of soil per acre Results of soil per acre n opm 61. 7 in. deep in ppm in 9-10 in. deep P x 2 tbs. per acre of P P x 3 - lbs, per acre of P x 4.6 lbs. per acre of Pao- x 6.9 bs: per acre of P..OS K x 2 Ibs, per acre or K K x 3 lbs. per acre of K' x 2A .= Ins' per acre of K 0 x 3.6 _ lbs. per acre of K20 Mg x 2 lbs. per acre of Ntg Mg x 3 - lbs. per acre df Mg Ca x 2 = 'Ibs. per acre of Ca Ca x 3 lbs. per acre of Ca S x 2 lbs. per acre of S S x 3 _ lbs. per acre of S S x 6 lbs. per acre of 304 S x 9 . = ibs. per acre of SO4 B. Zn, Mn, B. Zn. Mn, Fe, Cu, Me Fe, Cu, Mo x 2 = tbs. per acre of B, x 3 - ds. per acre of B, Zn, Mn, Fe, Cu, Me Zn, Mr. Fe. Cu. Me PHOSPHORUS Two different tests are made and reported for availability of phosphorus in tfre soil sample. Weak Bray (P1)-This method determines the amount of readily available phosphorus in the sail. A level of at least 20 ppm of P is desired for average crop production and a level of 30 ppm of P is desired for top yields of most crops. Strong Bray(P2)- This methoddeterrt nestheanpuntofreadilyavailable phosphorus plus a par of the active reserve phosphorus in the soil. A level of at least 40 ppin of P and preferably 60 ppm of P or more is desired for good yields of most crops. SODIUM BICARBONATE (P)-This method determines the amount of readily available phosphorus in calcareous soils (having free lime present). A level of at least 10 pprn of P and preferably 15 ppm of P or more is desired for good yields of most crops. For additional information of phosphorus availability and recommendation guides, see pages 13.21 in our book, 'Soland Plant Analysis.' CATION EXCHANGE CAPACITY (CEG) T he cation exchange capacity (C.E.C.) is a measure of the capacity of a soli to hold exchangeable cations. These include Hydrogen (H+), Calcium (Ca;-; }; Magnesium (fv1g+-r), Potassium (K.) and Sodium (Na-). C.E.G. is measured in terms of mill€equivalents (meq.) per 10C grams ofsoii. It depends largely on the amount and type o' clay present and the organic matter content. The larger this value; the more cations the soil is able to hold against leaching. PERCENT BASE SATURATION The balance for the soil colloid recommended by most soil scientistsis 65 to 75 percent calcium, 10 to 15 percent magnesium, and from 2 to 5 percent potassium. The percent base saturation is calculated from the C.E.C. and percent sauralon of Ca, Mg, K, H, and Na is reported to assist you in determining the balance of cations i- your soil. For additional Information and recommendation guide, see pages 25-29 in our book, "Soil and Plant Analysis.' pH Soil pH: The soil pH is measured on a 1:1 soil-towater solution. The soil pH measures the active soil acidity to a kalirfty. Mineral soils &.cold havea pH of 6.0 to 7.0 for most crops, :while a pH range of 5.0 to 5.5 is adequate for high organic soils. Buffer Index: The buffer pH is determined will the Shoemaker, McLean, and Pratt (SMP) buffer solution. The line requirement is determined by the depression o:` the buffer pH by acidity in the soil sample. The amount if limestone needed to neutralize the acidity present has already been determined and the following table js a general guide; but variations from other published guides may occur due to differences in limestone fineness, neutralizing value, and plow depth. SALT pH In areas whore the SMP buffer is tot used, a salt pH is determined. The salt pH of th soils is reasured by aiding 0.01 molar calcium chloride to the soil's solution, Soils which are highly leached and sandy soils may have a salt pH value as much as one who's unit lower than the sal pH. ;i.e. 6.0. 5.0). The soil pH value of soils of average salt content may be lowered from 0.4 to 0.6 units by using the calcium chloride. Depressions of the soil pH amounting to 0.1 units and less upon the addition of calcium: chloride occurs :when soils are excead'ngiy high in their content of sails. For additional information on soil DH and liming gufu'e, see pages 30-33 to our book, "Soil and Plant Analysis." LIME REQUIREMENT Buffer pH 7.0 6.9 • 6.8 r6.7 s 6.6 6.5 6A . 6.2 6.1 6.0 5.9 5.6 5.5 Tons;Acre Limestone Mineral Soils - Plow Depth Plow Depth 651s inches - :9 inches Organic Soils ' Plow Depth Plow Depth 6%1 inches 9 inches none none none none 0 0 1 - 1.5 0 0 1.5 2 •O: 0 2 a 3 c0' 0 2.5 4 0 0 3 4.5 1 1.5 3.5 Y 5 2 3 4 6 2.5 3.5 4.5 7 3 4.5 5.5 - 8 4 6 6 9 4.5 6.5 6:5 to 5 7.5 1 i 5.5 8 8 12 6 9 9 13 6.5 10 little soil pH is above 6.5, no buffer index will be determined since 'line would not be needed for most crops. Cropsmised on organic soils (soils containing 20 % or more organic matter) usually do not benefit from liming unless the soil pH 1s less than 5.3. ADJUSTMENTS FOR TYPE OF LIMING MATERIAL 9 Two primary factors affect the actual amount of a given iming_material required to achieve the desirable effect on soil pH. The total Nutrilizing Power (TNP, also referred to as Calcium Carbonate Equivalent) and the fineness of the liming material are these factors. The following tab':e will serve as a ggiid'e to make these adjustments. Ag Ag Ag Ag Ag Super- Pulverized Ag Fne Course Granulate Hydrated fine Base Ground Meal Mea Stag Lbs. to equal 1 ton of Limestone '1100 1900 2000 2300 2900 3400 2700 TNP 140-160 90+ 90+ 90> 90: 90+ 90+ F % I P N A 100 MESH 100' 80 6046 40 30 20 5 E S 60 MESH 100 95 70% 56 40 30 15 N S 20,fAESH 100 100 95% 70 60 50 50 E 1-, S N S G If the TNP is less than 90, multiply amount from above by these percentages: TNP 80-89 1115 70.79 130 60-69 150 LINING: _- Apply lime only after the soil has been tested. Too much � lime can be as harmful as too tittle. i:irne must be thoroughly mixed with the soil for maximum effectiveness, If both magnesium and calcium are needed, apply dolomite lime to help supply magnesium. EXCESS LIME: A visual rating of free lime present. Soils haying high amounts of free lime available will have associated problems in the availability of major and minor elements and difference in choice or amount of soil amendments. SOLUBLE SALTS: For information, rater to page 61 of our book, "Soif and Plant Anafysls SULFUR: All crops reed sulfur. The higher the nitrogen uptake by a crop, the greater the need for sulfur. A level of 15:20 ppm of available sulfur should be maintained for most crops. For additional information on availability of sulfur and making recommendations; see pages 22-24 in our book, `Soiland Plant Analysis.' MICRONUTRIENTS The available loves of mlcronutriertsare rated from very low to very high. However, applying the recommended amount of a certain manor element with a low rating krill not necessarily insure a crop response because of the many factors which mayiirfluence mielahutrient response. Some of the factors which influe%e response are: rapidly changing soil pf 1, excessive applications of N-P-K, soi; physical problems, soil moisture extremes, excessive leaching, crop variety, and plant population. For additional nforma5on on why plants hided midrorutrients, their availability, interactions wit'r, other nutrients and a recommendation guide. see pages 34-45 in our book. 'Soli and Plant Analysis.' "Our records and letters are for the exclusive and confidential use of our clients and may not be reproduced in whole or in part, nor may any reference be made to the work, the results or the company in any advertising, -news release, or other public announcements without obtaining ors:, prior written. authorization." Copyright 1977 REPORT NUMBER: R 2.15•_c)07 ADDITION SEND TO: DI O GRO DIVISION POS 388 PI NEVI LLE NC 281 34-0388 DATE OF REPORT t /t )7' 9f' PAGE 1 IN AGRICULTUE1 A L LABORATORIES, INC. IJPA ne Road • Richmond; Virginia 23237 • (804) 743-9401 Fax No. (804) 271-6446 GROWER: DONAL.D PAYNE — AL.5 SOIL ANALYSIS REPORT SAMPLES SUBMITTED BY: ACCT # 4 546' ROB[_-T T HAMILTON COPY TO: ANNAPOL.I 6, MD DATE" RECET VED 0.8/01 /96 DATE: OF ANPL.YS I S 09/02 /96 SAMPLE LAB Nitrogen Phos- phP s Potassium Sulfur Calcium Magnesium Sodium Iron Aluminum Manganese Copper Zinc Ammonia Nitrft (DENT. NO. N K S , Ca Mg Na -Fe AI Mn Cu Zn Nitrogen Nitrogen mglkg mpg mglkg mglkg mglkg mglkg mglkg m9 9 9 _ mg/kg m�9 9 m9�9 mg�9 1 20560 2 20561 W 20562 4 2t_J 563 5 2c_)564 LAB Cadmium . Chromium Nickel Lead Arsenic Mercury Selenium Organic Total Cd Cr Ni Pb As Hg Se .Nitrogen pH C.E.C. MO . NO. �g �g mg/kg �g �g mglk9 •. mg/kg mglk9 ( 100g) 2i 560 1 33 :: 5 9 3.96 0.09 0.35 <' 5 c t-)561 :: 1 33 5 14 3. 47 :0. C)J. 0. 32 ,; 5 20562 1 42 7 17 7.65 •::0.01 0.36 • rs;. 5 20563 1 29 r 5 14 5. 33 1`0, 01 0.33 < 5 20564 : 1 23 5 11 3.96 <:O.01 0.26 5 This report applies only to the sample(s) tested mples are Our reports and letters are for the exclusive and confidential use of our clients, and may not be reproduced In whole or In part, nor may any reference be made retained a jr M of thi¢�)¢ay� teatirIg.l, = 0 to the work, the results, or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization. pRl FASTFAN ArRlf 11{ TURAI 0afW RaTt4RIFR INr REPORT NUMBER: A&L EASTERN AGRICULTURAL LABORATORIES, INC. R22 5--087 7621 Whitepine Road • Richmond, Virginia 23237 - (804) 743-9401 Fax No. (804) 271-6446 SEND TO: BID GRO DIVISION FOBi 388 PINEVILLE NC 28134-0388 DATE OF REPORT 08 / 47 / 96 PAGE 2 GROWER: DONALD FAYNE— AL5 SOIL ANALYSIS REPORT ACCT # 45469 SAMPLES SUBMITTED ROBERT HAMI LTON BY, COPY TO: ANVAPOLIS, I DATE RECEIVED 08/01/96 DATE OF ANALYSIS 08/02/96 NRrogen Pho®- Potassium Sulfur M*kmt mum Sodkn Iron Aknighum Mm*ansee Capper Zanc AmmmnW Nil SAMPLE LAB N *PM K S Ca M9 Na Fe Al Nh Cu Zn MbWn Nitro IDEt�T. NO. mpg mpg g mgrKg ms" MOM rt9&9 moft +11109 MW 6 20565 7 20566 g 20567 9 20568 10 20569 LAB Cadmium Chromium Nit W Lead Arse* MOM" Selertlum Tonal MO Cd Cr Ni Pb As Hg Se Nill"M PH C.E.C. NO. nVkg mgtkg mgkg mg*g mpg nVkg mg&g nV*9 (n000g) 20565 1 25 5 13 3.69 <0.01 0.22 5 20566 1 35 5 10 S.82 <0.01 0.25 < 5 20567 1 42 10 29 9.07 <0.01 0.33 < 5 20568 1 52 12 24 7.85 <0.01 0.12 < 5 20569 1 48 10 17 8.98 0.11 0.13 < 5 This reportAplips only tot ) tad. S ;es are Our caponof ned ofs and letters are for the exclusive and confidential use of our clients, and may not be reproduced in whole or in part, nor may any reference be made retait to to the work, the results, or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization. A&L EA BO INC. REPORT NUMBER: A&L EASTERN AGRICULTURAL LABORATORIES, INC. R215-087 7621 Whitepine Road - Richmond, Virginia 23237 - (804) 743-9401 Fax No. (804) 271-6446 l SEND TO: D15 GRO DIVISION Poe "'.3aa PI NEVI LLE NC 23134--0388, 00/07/96 3 DATE OF REPORT PAGE SAMPLES DONALD F- A VNE -- AL5 SUBMITTED GROWER: BY: SOIL ANALYSIS REPORT r� ACCT # 456-69 ROBERT i- -41II__T01\1 COPY TO: Fti`11�,=;f='�tl_:[ �i, 10 DATE RECEIVED �;r?!tt1. i 96 DATE OF t24NAL'YSIf3 (' f3!i:?;�?'y' SAMPLE LAB � Nitrogen pho s- Potassium Sutfur Calcium Magnesium Sodium Iron Aluminum Manganese g �� r Zinc . Ammonia Nitrate (DENT. NO. N .. P K S Ca Mg Na Fe Al Mn Cu . Zn . Nitrogen Nitrogen m919 �g mg/kg mg1kg mglkg mg/kg mglkg. mt�lk9 Mg/kg m9�9, mg/kg, mg/kg m9lk9 mg/kg 1 1 2o57D 12 20571 13 20572 . 14 20573 15 2 t_)574 LAB Cadmium Chromium' Nickel' Lead Arsenic Mercury Selenium Organic Total, `- Cd Cr Ni Pb As Hg Se Nitrogen . pH C.E.C. NO. .. mglkg mg/kg mg/kg - _ mglkg mglkg mg/kg mglkg mgtkg (meg/100g) ; 2057o 1 61. 10 24 (3.09 0. 1'3 C). 1.:3 S 2 0571 :: 1 60 9 21 10.13 0.10 C1.13 20572 1 60 6 11 S. 89 < 0. 01 Cl. 13 w,< S 2(_)573 :. 1 40 5 12 6.40 <i0.01 0.11 c 20 574 1 3(3 6 1.3 6. 65 ;t Q. 01 O. 12 :: 5 ; " This report applies only to the sample(s) tested. Samples are Our reports and letters are for the exclusive and confidential use of our clients, and may not be reproduced In whole or in part, nor may any reference be made retainetlfflnq�_a, o} thir}y�a � atser tegtingq I:. to the work, the results, or the company In any advertising, news release, or other public announcements without obtaining our prior written authorization. A&L ER CULTURAL LAB RATORIES, INC. Y REPORT NUMBER: A&L EASTERN AGRICULTURAL LABORATORIES, INC. R215-097 7621 Whitepine Road • Richmond, Virginia 23237 • (804) 743-9401 Fax No. (804) 271-6446 (: SEND TO: 810 GRO DIVISION POB 38B PINEVILLE NC 28134-0398 DATE OF REPORT V8�t77�95�' PAGE 4 SAMPLES GROWER: DONAL.D PAYNE— AL5 SUBMITTED BY: SOIL ANALYSIS REPORT l� 0 ACCT # 4` 4->9 RI-JFtERT HAMIi._.TCIN COPY TO: Ar�isar�r't-)L_ [ Sy IvtiD DATE RECEIVED i `?,f ) DA'rE OF ANALYSIS i..J SAMPLE LAB Nitrogen N Phos- phorus Potassium Sulfur Calcium Magnesium Sodium Iron Aluminum Man anew 9 Copper Zinc Ammonia Nitrate (DENT. NO. mglkg P mglkg K mglkg S mglkg mglkg _ Mg mglkg Na mglkg Fe mglkg Al mglkg Mn mglkg Cu mglkg Zn mglkg Nitrogen mglkg Nitrogen mg/kg 16 20575 17 yy 20576 R 5 LAB Cadmium Chromium, Nickel. Lead Arsenic Mercury Selenium Organic Total NO. '. Cd mglkg. Cr mglkg Ni mglkg Pb mg1kg As mg/kg, Hg mg/kg Se mg1kg Nitrogen mgkg . pH. C.E.C. (mXV100g) MO 20575 :: 1 36 a 9 7.40 o.11 0.12 ;. 5 2(--)576 1 43 5 13 4. 49 ;fit. 01 0.11 5 Our reports and letters are for the exclusive and confidential use of our clients, and may not be reproduced in whole or in part, nor may any reference be made This report applies only to the sample(s) tested. Samples are to the work, the results, or the company in any advertising, news release, or other public announcements without obtaining our prior written authorization. retained axim f tth;¢ay� aver te�tin�,Il: h&L E�R G I ULTU AL LABORATORIES, INC. SOIL SERIES: BETHLEHEM PROFILE DESCRIPTION: The Bethlehem series consists of moderately deep, well drained soils on ridgeetops and side slopes in the Piedmont. These soils formed in .residuum weathered from sillimanite schist. Slopes range from 2 to 15 percent. Bethlehem soils -are commonly adjacent Hibritten, Pacolet, Rion, and Chwacla soils. SOIL SERIES: BUNCOMBE PROFILE DESCRIPTION: The Buncombe series consists of deep, excessively drained soils on flood plains, These soils formed in recent alluvium along the larger streams. They have a brown sandy surface layer, but they lack a B horizon. Slopes range from 0 to 8 percent, These soils are low in organic -matter content, natural fertility, and available water -holding capacity. They are strongly acid. The Buncombe soils occur with the Congaree soils. They are deeper, lighter colored, and coarser textured than the Congaree soils. SOIL SERIES: CECIL PROFILE. -DESCRIPTION: The Cecil series consists.of well drained, nearly level to steep soils on Piedmont uplands. Typically these soils have a sandy loam surface layer about 7 inches thick. The -subsoil is dominantly red clay and clay loam 43 inches thick. The underlying material is multicolored, loamy saprol'ite of acid _crystalline rock. Slopes range from 0 to 25 percent:` Bedrock is at a depth greater than 60 inches. SOIL SERIES: CHEWACLA PROFILE DESCRIPTION: The Chewacla series consists of somewhat poorly drained soils on nearly level flood plains. Typically, they have brown loam surface layers, 8 inches thick. The subsoil is 50 inches thick. It is dark yellowish brown and yellowish brown silt loam in the upper part, light yellowish brown loam in the middle part, and light brownish gray silty clay loam in the lower part. The underlying material is sand and extremely gravely sand. They formed in fluvial sediments. Slopes are 0 to 2 percent. Bedrock is at a depth greater than 60 inches. SOIL SERIES: DOGUE PROFILE DESCRIPTION: Dogue fine sandy loam, 2 to 8 percent slopes, rarely flooded. Thi very deep, moderately well drained soil is on gently sloping low stream terraces of the piedmont. Many areas are somewhat elongated and range from 4 to about 40 acres in size., Typically the surface layer is dark grayish brown fine sandy loam, 2 inches thick. The subssurface layer is brown fine sandy loam, 6 inches thick. The subsoil is 44 inches thick. It is brownish yellow clay loam in the upper part, brownish yellow clay with red and light gray mottles in the middle part, gray clay with strong -, clay loam with brownish yellow mottles in the lower part. The underlying material, to a depth of 60 inches, is light gray sandy clay loam. Dogue soil has moderately slow permeability and medium surface runoff from bare and unprotected areas, Shrink -swell potential of the subsoil is moderate. Depth to bedrock is greater than 6 feet. The seasonal high water table is 1.5 to 3 feet below the surface. The soil is subect to rare flooding. Soil reaction is extremely acid to strongly acid unless limed. SOIL SERIES: PACOLET PROFILE DESCRIPTION: The Pacolet series consists of deep well drained soils with a brown sandy clay loam surface layer and red clayey subsoil. These soils are formed from weathered rock and are commonly found on the piedmont uplands. They have slopes ranging from 2 to-25 percent. Pacolt soils are moderately permeable and slightly acid. The C horion consists of a multi -colored saprolite. They are,pommonly found near Rien, Wedowee, Masada,_ Chewacla, and Toccoa soils. SOIL'SEAIES: RIVERVIEW PROFILE DESCRIPTION: Riverview series consists of very deep well drained soils on flood plains in piedmont. Surface layer brc,;n fine sandy loam 10 inches thick. Subsoil 33 inches thick, yellow red silty clay loam. Seasonal high water 3 to 5 feet below the surface. r Town of Taylorsville Land Application Sites Attachment 8: Site Life Evaluations echnoloies Inc::.;............................................................................................ Wheelabrator Water T................:.;:.;:;.;Bio Gro Division g TOWN OF TAYL1m3vru.E LAB REPORT:R062-306 DOSAGE RATE EVALUATION PERMIT INFORMATION (LIFETIME RATES) CONCENTRATION LBS/DT Allowable Allowable PARAMETER (PPM) of Sludge Ibs/ac DT/AC PAN (inject) 39,219 78.438 100 - 200 1.27 2.55 PAN (surface) 32,469 64.938 100 - 200 1.54 3.08 P Phosphorus 13,900 27.800 K Potassium 6,100 12.200 Zn Zinc 346 0.692 2,492.0 cumm. Cu Copper 172 0.344 1,335.0 cumm. As Arsenic 0.8 0.002 36.5 cumm. Cd Cadmium 1.0 0.002 33.0 cumm. Cr Chromium 86.0 0.172 2,670.0 cumm. Pb Lead 17 0.034 267.0 cumm. Hg Mercury 0.390 0.001 14.0 cumm. Mo Molybdenum 5.0 0.010 16.0 cumm. NI Nickel 34 0.068 373.0 cumm. Se Selenium 1.16 0.002 89.0 cumm. Formulae: Plant Available N = ((f (ppm Org N)) + (ppm NH -N) +(ppm NO-N))0.002 (Inject) Plant Available N = ((f (ppm Org N)) + v (ppm NH -N) + (ppm NO-N))0.002 (Surface) parameter (lbs/DT) = parameter (ppm) x 0.002 PLANT AVAILABLE NITROGEN DT Sludge/AC Load/AC K CROP PAN Required (surface) (surface) #/AC Cam (Silage) 220 3.3 16.3 40.7 Cam (Grain) 220 3.4 16.4 41.0 Fescue/Hay/Pasture 250 3.8 18.8 47.0 Soybeans 150 2.3 11.3 28.2 Wheat & Barley 100 1.5 7.3 18.2 Clover/Alfalfa 250 3.8 18.6 46.4 Bermuda Grass 220 3.3 16.3 40.7 DT Sludge/AC Load/AC K CROP PAN Required (inject) (inject) #/AC Cam (Silage) 220 2.8 13.6 33.9 Cam (Grain) 220 2.8 13.5 33.6 FescuelHay/Pasture 250 3.2 15.5 38.7 Soybeans 150 1.9 9.3 23.2 Wheat & Barley 100 1.3 6.2 15.6 Clover/Alfalfa 250 3.2 15.6 38.9 Bermuda Grass 220 2.8 13.7 34.2 3,601.2 3,880.8 22530.9 16,600.0 15523.3 7,852.9 17948.7 1500.0 5,485.3 38362.1 I Input Data for Plant Available Nitrogen Ammonia Nitrogen % 1.35 Nitrate Nitrogen PPM 189 Organic Nitrogen % 8.51 Digestion Factor 0.3 Percent Solids 0.7 GL or CY / Load 6500 Dry Tons Per Load 0.20 TERMS: f = mineralization rate = Digestion Factor v = non volatilized fraction of NH - N = 0.50 PAN = Plant Available Nitrogen NOTE: This utilizes EPA Part 503.13 Standards or North Carolina Standards whichever Is the most stringent. CEC<5 P METALS: LIFETIME YEARS BASED ON PAN DT/AC Ibs/acre Cd Cu Zn Ni Pb As 92.8 4,943.3 yr •'"••'•'• yr •"""« yr 1,643.4 yr 2,352.7 yr 6,760.1 yr 93.3 4,913.9 yr ••"'"'"'" yr •«""'• yr 1,633.6 yr 2,338.7 yr 6,709.9 yr 107.0 4,285.9 yr •""""""'• yr 935.4 yr 1,424.8 yr 2,039.8 yr 5,852.4 yr 64.2 7,143.2 yr «"'""«• yr •••••"•"' yr 2,374.7 yr 3,399.7 yr 9,754.1 yr 41.4 11,074.3 yr "•'"•"'• yr ••'•••'•` yr 3,681.6 yr 6,270.7 yr 15,122.1 yr 105.6 4,342.3 yr ••"""••yr 947.7 yr 1,443.6 yr 2,066.7 yr 5,929.4 yr 92.8 4,943.3 yr «•"•""• yr •"•••""•' yr 1,643.4 yr 2,352.7 yr 6,750.1 yr CEC < 5 P METALS: LIFETIME YEARS BASED ON PAN DT/AC Ibs/acre Cd Cu Zn Ni Pb As 77.3 5,933.4 yr "'"""'""• yr ••••'"'"" yr 1,972.5 yr 2,823.9 yr 8,102.1 yr 76.6 5,989.6 yr ••"'"""'•yr •••"•"'"•yr 1,991.2 yr 2,850.7 yr 8.178.9 yr 88.2 5,199.7 yr "'""'••`yr ••"'"'"`yr 1,728.6 yr 2,474.7 yr 7.100.3 yr 52.8 8,691.8 yr «""«"yr •""•••"«yr 2,889.6 yr 4,136.7 yr 11,868.7 yr 35.4 12,942.3 yr "••'"•"' yr •'••••••• yr 4,302.6 yr 6,159.7 yr 17,672.8 yr 88.6 5,176.9 yr «"""'• yr ••'•"'•• yr 1,721.0 yr 2,463.9 yr 7,069.1 yr 78.0 5,882.9 yr •"'"'"« yr •""•••« yr 1,955.7 yr 2,799.9 yr 8,033.1 yr Se Mo Hg Cr 11,493.1 yr 449.4 yr 5,377.3 yr 4,650.7 yr 11,424.6 yr 446.7 yr 5,345.3 yr 4,623.0 yr 9,964.6 yr 389.6 yr 4,662.2 yr 4,032.2 yr 16,607.7 yr 649.4 yr 7,770.4 yr 6,720.3 yr 25,747.6 yr 1,006.8 yr 12,046.7 yr 10,418.8 yr 10,095.7 yr 394.8 yr 4,723.6 yr 4,085.3 yr 11,493.1 yr 449.4 yr 6,377.3 yr 4,650.7 yr Se Mo Hg Cr 13,795.0 yr 539.4 yr 6,454.4 yr 5,582.2 yr 13,925.7 yr 544.5 yr 6,515.5 yr 5,635.1 yr 12,089.3 yr 472.7 yr 5,656.3 yr 4,891.9 yr 20,208.2 yr 790.2 yr 9,456.0 yr 8,177.3 yr 30,090.4 yr 1,176.6 yr 14,078.6 yr 12,176.1 yr 12,036.2 yr 470.6 yr 5,631.4 yr 4.870.5 yr 13,677.5 yr 534.8 yr 6,399.4 yr 5.534.6 yr or 1 TvResidual PAPS Available" Report Amount Remaining Naeidual PAN Balance Balance in rr0-N up�mara Aced Aliaezalinad Ava,ylable Thie^---r-119-6)----- Year Or9-N Lbe/Agra Rate of 0rd^p Lba/fie ---_ <e> Lbe/Acre tlaavin9> __ ---- 1me/Aare ^..� o! APP 1 APPLied --^- '--^_-�'`� -__ -----' _ _ $i.oeolide 2gPa ---^' ---- - -- ------ _20 -------- Lally minera]iee , Field SA ___ - ---_"------ — ---- 1992 T®1e ORg-N' bee been 17 laavino 190 ------------------- W_AL-00002-0-0002 2080 O1L1Q 30.00 'b o! 27 leaving -> 12 Lbe Per Acrs 2994 257 2995 1995 15.00 % of 180 � 12 <--------'-- 959 1996 0.00Ib of 1 laavimg 0 Lbe Par Aare 2 1995 30.00 'd of 2 -_-- 1 0 <------- ----- 1995 1996 15.00 IA Of o Yinaraliaatlwo Traokadl•----------------------. "------- lioatiome " 12 yba Per Acre Corr mt Year APPlioatlan IN ------------------- , ----'-----P 1996 --------'__-_--" PAN Available in 1996 from Prior Xoare' _----"---'---' -----------'----^'---- _---__- g�arp !oz Field NC-AL00002-0- Total flaaidnal O "Residual PAN Available" Report Year of Riold M Rioealida Type Appl Orp-V Lbw/Aare Applied Rate Hinecaliaed <nt> ---- ®alanoe of Orq-If Lbe/flora ------------ Aoovnt of Orp-N lEineralised o-> 1ba/Aace --- ------------ Remainlno Balanoe Vaninerel3eed <leavinO Lba/Acre ---- --------- ---------- Residual PAN A+ailable lbia Year (19961 -- ------------------- NC-AL-00002-0-0001 2080 O1L10) 1995 150 1996 15.00 • of ill . l7 a 17 lervin I11 <----------------------- > 17 Lbe Par Aare ------------------- O p M W 1996 3 Cd=ent Year Applieatiom (No Hineraliaatiom Teackedl. --------------------------------- -_^------ .=y f996 tram Prior Yeaze' Applioatione 17 Lbe Per Acre or M61d LTC-AL-00002-0-0001 .. Dotal ReaidOal PAN Available 1n 1 Town of Taylorsville Land Application Sites ..... ....... ......... . ........... ................. ......... Section 3.0 Site Specific Information Site Summary Sheet Site AL4 Site AL5 ............... X Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites SITE SUMMARY SHEET Town of Taylorsville SITE GROSS ACRES NET ACRES AL4 61.5 50.0 AL5 236.8 217.5 Total 298.3 267.5 ....................................................................................... Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites ......... .; ... ; ........ ..... ... ............. ..... .......... X XXX .. .. ......... - -.:- M ................................... ........... ............. .. ......... .. ....... ......................... . ............. ................. .. ...... ......................... "I .. ..... Site AIL4 Request and Consent for Biosolids Site Summary Sheet Field Data Sheets Vicinity Map Site Map Topographic Map Soils Map Flood Plain ............ ..... ........ .............. . . ... ......... ........... .... . .. ....... ....... Wheelabrator Water Technologies Inc. Bio Gro Division Town of TV-orsville . .. ....... . Land Application Sites . .. ............... . . .. ........... . . . ........................ .................. ................ * ......... Request and Consent for Biosolids . ........ ....... .................. .. - " ­ .. .: ...... ...... .......... :.":. Wheelabrator Water Technologies Inc. Bio Gro Division J B10 �`Division AskWheelabrator Clean Water Systems Inc. REQUEST AND CONSENT FOR BIOSOLIDS SOURCE: FARM OPE ADDRESS: PHONE: ( 6 Sa ) FARM LOCATION: TOTAL ACREAGE: COUNTY- CROPS: 1. I agree to be responsible for adhering to the following conditions, where applicable: a. The soil pH will be adjusted to> 0 when biosolids are applied. (This may be accomplished_ through the application of lime -treated biosolids.) b. Do not graze animals on the land for 30 days after the application of bios lids. In addition, animals intende'dJor d3i y production shall not be allowed to graze on the land for 3 O days a er the application of biosolids. c. Food crops with hafvested parts that touch the biosolids/soil mixture and are to ally above the land surface shall not be harvested for 2 Lf months after the application of biosolids. \ // d. Food crops with harvested parts below the surface of the land shall not be harvested for Z .6a months after the application of biosolids when the biosolids remain on the land surface > 4 months prior to incorporation into the soil, or 38 months when the biosolids remain on the land surface < 4 months prior to incorporation. e. Food crops, feed crops, and fiber crops shall not be harvested for 30 days after application of biosolids. f. Public access to land with a low potential for public exposure shall be restricted for days. Public access to land with a high potential for public exposure shall be restricted for 1 year. g. Turf grown on land where biosolids are applied shall not be harvested for one year after application of biosolids when the harvested turf is placed on either land with a high potential for public exposure or a lawn, unless otherwise specified by the permitting authority. 2. 1 understand that this transaction is not contemplated by the parties to be a sale of goods, and that Wheelabrator Clean Water Systems Inc. - Bio Gro Division (hereinafter Bio Gro) is willing to provide to me without charge the service of land applying biosolids which have been approved by the appropriate regulatory agencies for land application. 3. 1 understand that successful crop production depends on many variables, such as weather, soil conditions and specific farming practices and that while Bio Gro has experience with land application of biosolids, the responsibility for properly accommodating agricultural practices to biosolids utilization are solely mine. I have also read and understand the "Important Information About Using Biosolids as a Fertilizer" which is on the reverse side and incorporated by reference in this Request and Consent. , OPERATOR'S SIB - - DATE' ❑ WCWS-Bio Gro Division • 900 Fox\Valley Drive, Suite 210 Longwood, FL 32779 • 407/682-2272 ❑ WCWS-Bio Gro Division • 12701 Lancaster Highway • Pineville, NC 28134 ^ 704/542-0937 BGDRQNC • 5/95 WHITE: Regional Office CANARY. Farmer IMPORTANT INFORMATION ABOUT USING BIOSOLIDS AS A FERTILIZER Biosolids Generation Biosolids are the accumulated, treated solids that are separated from water during the wastewater treatment process. Biosolids are produced by public and private wastewater treatment plants (Generators). The Generator is responsible for supplying biosolids that are suitable for land application according to state and federal specifications. Benefits of Biosolids Biosolids provide nitrogen in a form that can be taken up by plants during their growth cycle. Biosolids also add phosphorus to the soil. If lime is added to biosolids, the biosolids will have the added benefit of a liming agent. Biosolids contain many primary, secondary and micronutrients that can be used by plants. Biosolids are primarily an organic material; when added to soil, they improve water and nutrient retention, reduce erosion potential and improve soil structure. The Permitting Process Once the farm operator requests biosolids, a Bio Gro representative initially-evaluates.the farm, for ttuck access and field conditions. If the farm is found to be suitable and the Request for Biosolids and the Consent for Biosolids forms are signed, Bio Gro will collect soil samples and have them analyzed by an independent laboratory. Bio Gro will then apply for any federal, state or local permits required for biosolids application. The permits will specifically identify the fields to which biosolids will be applied and will be issued to Bio Gro or the Generator. After the permits are obtained (a process that may take several months or more) Bio Gro will apply biosolids, as they become available, to the fields. Availability of biosolids may vary because of weather conditions; contractual arrangements with biosolids generators and other factors. Although the company cannot guarantee biosolids application because of factors beyond its control, Bio Gro will use its best efforts to apply biosolids to the permitted fields. The conditions outlined in the permit will apply to ariy and all biosolids applications made by Bio Gro. Bio Gro will not be responsible for biosolids applications made by any other entity. Periodic visits to the land application site(s) by federal, state and local regulatory staff and Bio Gro representatives may occur for the purpose of permitting the site, inspecting the site, applying biosolids, obtaining samples at the site and testing. Proper identification will be provided upon request. Agronomic Considerations Tractor -trailer units are used to deliver biosolids to the fields approved for biosolids applications. Soil compaction may occur on the travel areas used by the trucks and in areas where biosolids is unloaded for transfer to the applicator vehicle. Since some biosolids contain lime, it is important to recognize any increase in soil pH where biosolids have been applied and exercise care in using certain herbicides. If considering the use of a sulfonylurea herbicide, particular attention should be paid to any label restrictions. High soil pH and dry weather may slow decomposition of these chemicals, resulting in carry-over. For soils with low manganese levels, increased soil pH from lime addition (alone or in lime treated biosolids) may reduce manganese availability and thereby potentially reduce crop yields. In planning a herbicide program, it should be noted that seeds may sometimes survive the biosolids treatment process — for example, tomato seeds. Also, the organic matter additions from biosolids application (organic matter tends to tie up certain herbicides) may require increased herbicide application rates. Consult your extension agent or chemical representative for a specific recommendation. Biosolids contain salts. Biosolids applications alone rarely cause salt problems. However, if combined with other significant salt -increasing factors, such as drought, excessive soil compaction, saline irrigation water and salt -containing fertilizers, salts may reach levels that could negatively affect germination and growth of some crops. While odor from biosolids applications are not usually significant, and typically less than that from livestock manure, it is possible that an odor from the decomposition of organic matter may be noticed. If this occurs, it generally disappears in a short time. Since biosolids provide nitrogen that will be released slowly throughout the growing season with diminishing carry-over in subsequent years, it is important to reduce the use of nitrogen and other fertilizers to appropriate levels. Town of Taylorsville Land Application Sites Site Summary Sheet Wheelabrator Water Technologies Inc. Bio Gro Division Town of Tavlorsville Land Application Sites SITE SUMMARY SHEET Site AL4 FIELD GROSS ACRES NET ACRES OWNER William H. Marshall Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites Field Data Sheets Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI-4-1 ACRES Gross 24.8 Net 23.1 OPERATOR Robert L. Marshall OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina/Hiddenite, North Carolina LATITUDE: 35055'30" LONGITUDE: 81007-30" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 and 4 PREDOMINANT SOILS Cecil Sandy Clay Loam (CeBz) ............ Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI-4-2 ACRES Gross 23.5 Net 15.5 OPERATOR Robert L. Marshall OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina/Hiddenite, North Carolina LATITUDE: 35055'30" LONGITUDE: 81 °07'30" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 and 4 PREDOMINANT SOILS Cecil Sandy Clay Loam (CeBz) ...................................................... :.;;:;.;;;:.;:««.;:;;.;;;:.;:.;:.;;::.::.::.;;;::::.;:.;::;:.;;::>::>::>::>:«:<:::.;>::>:.>:.>::>:::>:::::::::::::::.;:.;;::<::.;:::.::::.;::.;;:.;:.;:;:.;:.;:.;::<:;:;:«.;:.>::.;;:.;:.>:.;:.::.;: Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AL4-3 ACRES Gross 13.2 Net 11.4 OPERATOR Robert L. Marshall OWNER Robert and William Marshall COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carol ina/Hiddenite, North Carolina LATITUDE: 35°55'30" LONGITUDE: 81 °07'30" SOIL SURVEY USDA Alexander Co. SHEET NO. F3and 4 PREDOMINANT SOILS Cecil Sandy Clay Loam (CeBz) .......... .......................................................................................................................................................................................................................................::;:.;:.;::.;;:.: Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites Vicinity Map Wheelabrator Water Technologiies Inc;.;:.;;:........................................................... ...................................................... .. n :.::.:::::::::::::.::::::::::::::::::::::::::::::::::..::.::::.;:.;:.;:.::.::;;;;;::::.::.:::.::......:..... . g Bio Gro Division I Heelabrab- Clean Water Systems Inc. RA Division SCALE: 1" = 2 miles A WHEELABRATOR TECHNOLOGIES COMPANY VICINITY MAP Land Application • BI0*F1X Alkaline Stabilization IPS Composting • Drying and Pelletizing Southern Region 908 Belcher Drive Pelham, AL 35124 205.664.8440 205.664.7678 Fax Site AL4 N PRINTED ON RECYCLED PAPER Town of Taylorsville Land Application Sites .......... I ....... .... .. .... . ....... . . ........ ......... . ...... ..... .. ... .......... ....... . ..... Site Map . . . .... .... X.: ....... ...... .......... ....... .... . Wheelabrator Water Technologies Inc. Bio Gro Division %� \%� � CJ � ��` ; � � �}%!�§ ����/ \�^� � ~� f� z % ® ® % g.<7 • , /\;//� � , : ». , -� �%� �\/§� J�'Z: ©,. ii, . a/./2�> �`�w\\���^� ¥ � «� @�« /� \ �� �� \� j\\§ ,t� V d (6� ,. " .� � . //. %^' « ,4 ~ `:�� � !3� � 2j� .� y. y« 6 �. » ��,�:; 223� ,9,w a. �� J��2\/99� / 2}:�- \�:� � � ®:ram w »^f � / \� . a {� § > f �� ' \: \; %�� \£� 2\� ' y,/k� /.2• v )�:\�/�/�:( ` :'_>� � : � �\> w � —/¥ ��/\\G���\ w, ���d�� \� \ \/ �2\�sw. )� �\�� \/ � � �'t:w\,ate. 4J%3/ ®`� ?»� ' �� \ � � \� \ \�\' � k �\ ^�w y�}>4 .e/\« �� ��( yy,aw��. z» 2 Ja Q � \ ,� j >`; /\2� /z .\� z�� � � ; / �:�,/ , .�.,�6 /�/ w{�ƒ2� :yG�.. �; Town of Taylorsville Land Application Sites Topographic Map ......... . . . . . . . ......... . . ....... .... .......... ............. . .............. .......... . . .. Wheelabrator Water Technologies Inc. Bio Gro Division /A Wheelabrator Clean Water Systems lnc. BAGH0 vi ' SCALE: 1:24,000 Southern Region 908 Bcicher Drive Pelham, AL 35124 205.664.8440 205.664.7678 Fax 30sm Site AL4, Fields 1, 2, and 3 TOPOGRAPHIC MAP Land Application • BID*M Alkaline Stabilization A WIME..LADRATOR ]ECHNOLOOIES COMPANY IPS Composting • Drying and Pelletizing ICJ PRINTED ON RECYCLED PAPER Town of Taylorsville Land Application Sites Soils Map ::.:::.:::.::.::.::.::.::.::.::.:::.::::.:::; ......... ......... ...................... Wheelabrator Water Technologies Inc. Bio Gro Division ' � •1 s p"j�� i 'rew 4 WIN b' �10F�,�.. 1 y�` y kMsomw .9 L 1 a , � i i�Jjjr g � I P"�1e ^'.f �� . �i �'� a �. I't '�. r 4 �r � J• 01 MR �i y� � ✓ , � �,, ` :Ifs .f� P �a �r �,q s�1w' �t. • 'r „�'�a� t t�. at � c� '�'��p' aL+ �� 7 "°� Town of Taylorsville Land Application Sites Flood Plains No fields for Robert L. Marshall (AI-4) are located within the 100 year flood plain. .................... ............. .......................................................: ::.:.... :::.:::<.;:....................... ........................................:.;:.;;:.::;:.;;:;.;:............................................ .................. . Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites ........... .. ... . . ......... ....... ............... .. . . .. .... . .... ... ..... Site AL5 Request and Consent for Biosolids Site Summary Sheet Field Data Sheets Vicinity Map Site Map Topographic Map Soils Map Flood Plain ..... ....... ... ................ Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites Request and Consent for Biosolids ..... ..:............................................... Wheelabrator Water Technologies Inc. Bio Gro Division REQUEST AND CONSENT FOR SIOSOLIDS SOURCE: i FARM OPERATOR:_ J VoNld �� '�� ADDRESS: -- pp LEI N _S/o`� e PHONE: 72, Z 3 FARM LOCATION: TOTAL ACREAGE: COUNTY: A $G.�I,yi, r?, CROPS: S0 1. 1 agree to be responsible for adhering to the following conditions, where applicable: a. The soil pH will be adjusted to ) when biosolids are applied. (This may be accomplished through the application of lime -treated biosolids.) b. Animals shall not be allowed to graze on the land for 30 days after the application of biosolids. In addition, animals intended for dairy production shall not be allowed to graze on the land for /) days after the application of biosolids. r C. Food crops with harvested parts that tquch the biosolids/soil mixture and are totally above the land surface shall not be harvested for f I months after the application of biosolids. d. Food crops with harvested parts below the surface of the land shall not be harvested for Z & months after the application of biosolids when the biosolids remain on the land surface >_ 4 months prior to incorporation into the soil, or 38 months when the biosolids remain on the land surface < 4 months prior to incorporation. e. Food crops, feed crops, and fiber crops shall not be harvested for 30 days after application of biosolids. f. Public access to land with a low potential for public exposure shall be restricted for �� v days. Public access to land with a high potential for public exposure shall be restricted for 1 year. g. Turf grown on land where biosolids are applied shall not be harvested for one year after application of biosolids when the harvested turf is placed on either land with a high potential for public exposure or a lawn, unless otherwise specified by the permitting authority. 2. 1 understand that this transaction is not contemplated by the parties to be a sale of goods, and that Bio Gro Systems is willing to provide to me without charge the service of land applying biosolids which have been approved by the appropriate regulatory agencies for land application. 3. 1 understand that successful crop production depends on many variables, such as weather, soil conditions and specific farming practices and that while Bio Gro has experience with land application of biosolids, the responsibility for properly accommodating agricultural practices to biosolids utilization are solely mine. I have also read and understand the document entitled "Important Information About Using Biosolids as a Fertilizer" which is on the reverse side and incorporated by reference. OPERATOR'S SIGNATURE DATE /6 ❑ Bio Gro Systems, Inc. • 900 Fox Valley Drive, Suite 210 • Longwood, FL 32779 • (407) 682-2272 ❑ Bio Gro Systems, Inc. • 12701 Lancaster Highway, Pineville, NC 28134 • (704) 542-0937 BGSRQNC-9/93 WHITE - Regional Office CANARY— Farmer IMPORTANT INFORMATION ABOUT USING BIOSOLIDS AS A FERTILIZER Biosolids Generation Biosolids are the accumulated, treated solids that are separated from water during the wastewater treatment process. Biosolids are produced by public and private wastewater treatment plants (Generators). The Generator is responsible for supplying biosolids that are suitable for land application according to state and federal specifications. Benefits of Biosolids Biosolids provide nitrogen in a form that can be taken up by plants during their growth cycle. Biosolids also add phosphorus to the soil. If lime is added to biosolids, the biosolids will have the added benefit of a liming agent. Biosolids contain many primary, secondary and micronutrients that can be used by plants. Biosolids are primarily an organic material; when added to soil, they improve water and nutrient retention, reduce erosion potential and improve soil structure. The Permitting Process Once the farm operator requests biosolids, a Bio Gro representative initially evaluates the farm for truck access and field conditions. If the farm is found to be suitable and the Request for Biosolids and the Consent for Biosolids forms are signed, Bio Gro Systems will collect soil samples and have them analyzed by an independent laboratory. Bio Gro Systems will then apply for any federal, state or local permits required for biosolids application. The permits will specifically identify the fields to which biosolids will be applied and will be issued to Bio Gro Systems or the Generator. Afterthe permits are obtained (a process that may take several months or more) Bio Gro Systems will apply biosolids, as they become available, to the fields. Availability of biosolids may vary because of weather conditions; contractual arrangements with biosolids generators and other factors. Although the company cannot guarantee biosolids application because of factors beyond its control, Bio Gro Systems will use its best efforts to apply biosoiiasiio the permitted fields. The conditions outlined in the permit will apply to any and all biosolids applications made by Bio Gro Systems. Bio Gro Systems will not be responsible for biosolids applications made by any other entity. Periodic visits to the land application site(s) by federal, state and local regulatory staff and Bio Gro Systems representatives may occur for the purpose of permitting the site, inspecting the site, applying biosolids, obtaining samples at the site and testing. Proper identification will be provided upon request. ronomic Considerations Tractor -trailer units are used to deliver biosolids to the fields approved for biosolids applications. Soil compaction may occur on the travel areas used by the trucks and in areas where biosolids are unloaded for transfer to the applicator vehicle. Since some biosolids contain lime, it is important to recognize any increase in soil pH where biosolids have been applied and exercise care in using certain herbicides. If considering the use of a sulfonylurea herbicide, particular attention should be paid to any label restrictions. High soil pH and dry weather may slow decomposition of these chemicals, resulting in carry-over. In planning a herbicide program, it should be noted that seeds may sometimes survive the biosolids treatment process —for example, tomato seeds. Also, the organic matter additions from biosolids application (organic matter tends to tie up certain herbicides) may require increased herbicide application rates. Consult your extension agent or chemical representative for a specific recommendation. Biosolids contain salts. Biosolids applications alone rarely cause salt problems. However, if combined with other significant salt -increasing factors, such as drought, excessive soil compaction, saline irrigation water and salt -containing fertilizers, salts may reach levels that could negatively affect germination and growth of some crops. While odor from biosolids applications are rarely significant, and typically less than odor from livestock manure, it is possible that an odor from the decomposition of organic matter may be noticed. If any odor occurs, it generally lasts for a few days or less. Since biosolids provide nitrogen that. will be released slowly throughout the growing season with diminishing carry-over in subsequent years, it is important to reduce the use of nitrogen and other fertilizers to appropriate levels. Town of Taylorsville Land Application Sites Site Field Summary Sheet Town of Taylorsville Land Application Sites SITE SUMMARY SHEET Site AL5 FIELD GROSS ACRES NET ACRES OWNER 1 11.8 10.3 Donald G. Payne 2 12.2 11.8 Donald G. Payne 3 13.4 12.9 Donald G. Payne 4 14.8 12.8 Donald G. Payne 5 12.6 12.5 Donald G. Payne 6 12.2 12.1 Donald G. Payne 7 12.2 12.1 Donald G. Payne 8 6.0 6.0 Donald G. Payne 9 81.1 73.0 Donald G. Payne 10 8.5 7.4 Donald G. Payne 11 6.9 6.0 Donald G. Payne 12 6.3 5.2 Donald G. Payne 13 5.8 4.5 Donald G. Payne 14 4.2 3.4 Donald G. Payne 15 9.1 7.8 Donald G. Payne 16 11.4 11.4 Donald G. Payne 17 8.3 8.3 Donald G. Payne Total 236.8 217.5 .......:................................................................................................................................................ ..................................................................................... Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites Field Data Sheets Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI-5-1 ACRES Gross 11.8 Net 10.3 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) ....:...............................::.;: «<:.;::.;:::<.;:.::.;:.;:.;:.;:.;:.:::.::.;:.;;;;:.;:.;;;::.;:.;:.;;: <.;:.;:<.;:................................................................................::::::::::::::::.:::::::.:::::::::.::::::::::::::....:.:::.:: . Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AL5-2 ACRES Gross 12.2 Net 11.8 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) ............. ............ ............:::;:::::.>;::<::;:.............................;;:.;:.;:.;;;:.;;:::.........................................................................:::>::»» ;..........................::....::.::.:::. Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI-5-3 ACRES Gross 13.4 Net 12.9 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 350 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) .......:........................................................................................................... ................ ................... .............................................................::.::.: Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AL5-4 ACRES Gross 14.8 Net 12.8 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) ................................................................................................................................................. Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI-5-5 ACRES Gross 12.6 Net 12.5 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) ......... Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AL5-6 ACRES Gross 12.2 Net 12.1 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 810 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) .....................................................:.;::;;;:.;:.;;:.;;;................:.;:;:.;;:...............................:::.:.;;;;::::::::.:............ ...:;.;;:.;: ;>;::>:.>::>::>::>::>:<:;::>:.;::::.......:::.:::::::::::::::::: . Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI-5-7 ACRES Gross 12.2 Net 12.1 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) X. ...:...............................:::.:::.;:;;:.;;::::....................................... ........................... ........................ .............................. ... ..........................::::::: . Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AL5-8 ACRES Gross 6.0 Net 6.0 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 350 52' 30" LONGITUDE: 81' 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AL5-9 ACRES Gross 81.1 Net 73.0 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 810 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) ...... Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites ................................................................................................................................................................................................................................................... . FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI5-10 ACRES Gross 8.5 Net 7.4 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 350 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) .......:........................................................................................................................................................................................................................................... . Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI5-11 ACRES Gross 6.9 Net 6.0 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) ........................ .................. .............................................................................................................................................................................................................. Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AL5-12 ACRES Gross 6.3 Net 5.2 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 810 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) ............. Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI5-13 ACRES Gross 5.8 Net 4.5 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) XXXX...................................................................... Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI5-14 ACRES Gross 4.2 Net 3.4 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) Wheelabrator Water ies Technolog;. Inc. :::«<................................................................................................................. .. � ��Bio��G�ro��Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI5-15 ACRES Gross 9.1 Net 7.8 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 350 52' 30" LONGITUDE: 81 ° 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Cecil sandy clay loam (CeBz) ............. Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AL5-16 ACRES Gross 11.4 Net 11.4 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylotsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 810 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 PREDOMINANT SOILS Pacolet sandy clay loam (PeBz) Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites FIELD DATA SHEET PROJECT Town of Taylorsville FIELD NUMBER AI5-17 ACRES Gross 8.3 Net 8.3 OPERATOR Donald G. Payne OWNER Same COUNTY Alexander TOPOGRAPHIC QUAD Taylorsville, North Carolina 1970 LATITUDE: 35' 52' 30" LONGITUDE: 810 08' 20" SOIL SURVEY USDA Alexander Co. SHEET NO. 3 .PREDOMINANT SOILS Pacolet sandy clay loam (PeBz) .......:........................................................................................................................................................................................................................................... . Wheelabrator Water Technologies Inc. Bio Gro Division Town of Taylorsville Land Application Sites Vicinity Map ................................................................................................................................................................................................................................................... . Wheelabrator Water Technologies Inc. Bio Gro Division Wheelabrator Clean Water Systems Inc. VICWITY MAP Southern Region 908 Belcher Drive Pelham, AL 35124 205.664.8440 205.664.7678 Fax iLand Application • BIO*FIX Alkaline Stabilization N A WHEELABRATOR TECHNOLOGIES COMPANY IPS Composting • Drying and Pelletizing PRINTED ON RECYCLED PAPER . (. Town of Taylorsville Land Application Sites .......... ..... ...... . ...... ............ . . ................... Site Maps ...... ... -X-: ........ . ........... ........ .. Wheelabrator Water Technologies Inc. Bio Gro Division 9 A Wheelabrator Clean Water Systems Inc. A&MODivisioa SITE MAP Southern Region 908 Belcher Drive Pelham, Al. 35124 205.664.8440 205.664.7678 Fax Land Application • BIO*FIX Alkaline Stabilization A WHEELABRATOR TECHNOLOGIES COMPANY HIS Composting Drying and Pelletizing PRINTED ON RECYCLED PAPER Fm Town of Taylorsville Land Application Sites Topographic Maps Wheelabrator Water Technologies Inc. Bio Gro Division I A& Wheelahrator Clean Water systems lnc. BI � oo Southern Region 908 Belcher Drive Pelham, AL 35124 205.664.8440 201.664.7678 Fax Site AL5, Fields 1 through 17 TOPOGRAPHIC MAP Land Application • BIO*FIX Alkaline Stabilization A wnECLABRATOR TF.('IINOI.OGfFS COMPANY IPS Composting • Drying and Pelletizing N PRINTED ON RECYCLED PAPER Town of Taylorsville Land Application Sites ...... .. ............ ............. .............. ............ ............... ............. ............ ................................ ............ . .................................................. ... . .... .......... ........ Soils Maps . ..... ..... .. ...... . W..... ...... ...... .... .... ... ..... heelabrator Water Technologies In'c"'.' Bio . Gro Division AL. Wheelahrator Clean Water Systems Inc. ®Div�sron SOILS velar r Southern Region 908 Belcher Drive Pelham, AL 35124 205.664.8440 205.664.7678 Fax Land Application BIO*FlX Alkaline Stabilization N A WHEELABRATOR TECHNOLOGIES COMPANY IPS Composting • Drying and Pelletizing PRIMPED ON RECYCLED PAPLK 77 Town of Taylorsville Land Application Sites ... . .. ... Flood Plains No fields for Donald Payne (AL5) are located within the 100 year flood plain. Wheelabrator Water Technologies Inc. Bio Gro Division