Loading...
HomeMy WebLinkAboutNC0001970_2020 Annual Report (Chloride Reduction)_20210318Strickland, Bev From: James Joyner <jjoyner@daa.com> Sent: Thursday, March 18, 2021 2:38 PM To: Smith, Danny Cc: Brock, Donovan Subject: Bay Valley Foods Chloride Reduction Report Attachments: RPT 21 0312 Chloride Reduction_Final.pdf WARNING - External email; exercise caution Attached please find the Bay Valley Foods Chloride Reduction Report for 2020. Please let us know if you have any questions. Thanks. James Y. Joyner, II NC Environmental Team Leader Draper Aden Associates Engineering • Surveying • Environmental Services Lasting Positive Impact® Phone: 919.582.7280 • Mobile 910.431.5870 daa.com i Draper Aden Associates Engineering • Surveying • Environmental Services 114 Edinburgh SOuth Drive Suite 200 Cary, North Carolina 27511 919.827.0864 www.daa.com March 15, 2021 Mr. Danny Smith, Director Division of Water Quality North Carolina Department of Environmental Quality 1617 Mail Service Center Raleigh, North Carolina 27669-1617 Re: 2020 Annual Chloride Reduction Report Bay Valley Foods, LLC — Faison, North Carolina 354 N. Faison Avenue, Faison, North Carolina NPDES Permit No. NC0001970 Draper Aden Associates Project No.: 2100309 Dear Mr. Smith, Via email: danny.smith@ncdenr.gov On behalf of Bay Valley Foods, LLC, Draper Aden Associates is pleased to present the 2020 Annual Chloride Reduction Report. In accordance with Special Condition A. (5) b.: NPDES Permit No. NC0001970, Bay Valley Foods, LLC-Faison, NC, continues efforts to study and evaluate chloride removal technologies and chloride reduction strategies. Enclosed please find a copy of the facility's 2020 Annual Chloride Reduction Report. As stated in previous reports, through the 1980's, 1990's and 2000's significant investments were made on process improvements, new equipment purchases, and process change strategies aimed at reducing salt use and subsequent chloride discharges. Notable investments and process changes include the replacement of wooden fermentation tanks, reduction of salt concentration in brines, process automation, and brine recycling technology. The early efforts resulted in substantial reduction in salt use with subsequent focus on pollution prevention efforts further reducing chloride discharges to surface water. As noted in previous Annual Chloride Reduction Evaluation Reports, there have been no economically feasible advances in chloride removal technologies applicable to the production processes employed at Bay Valley Foods, LLC — Faison, NC. Efforts continue to improve process control/automation focused on reducing brine loss and salt waste. If you have any questions or comments, please contact us at 919-582-7271. Sincerely, Draper Aden Associates James Y. Joyner, II, RSM Candy E. Elliott, P.G. Team Leader Project Geologist Enclosure cc: Mr. Donovan Brock (1 HC) Blacksburg • Charlottesville • Manassas • Newport News • Richmond • Virginia Beach Fayetteville • Raleigh 2020 Annual Chloride Reduction Report Bay Valley Foods, LLC - Faison, NC NPDES Permit No. NC0001970 DAA Project Number 2100309 March 15, 2021 Prepared for Bay Valley Foods, LLC 354 N. Faison Avenue Faison, North Carolina 28341 Prepared by Draper Aden Associates 114 Edinburgh South Drive Cary, NC 27511 Draper Aden Associates Engineering • Surveying • Environmental Services 3RD PARTY REVIEW This Report has been subjected to technical and quality reviews by: Candy Elliott Candy Elliott, PG Project Geologist William D. Newcomb, PG William D. Newcomb, PG Senior Program Manager Signature F� Signature March 12, 2021 Date March 10, 2021 Date March 15, 2021 James Y. Joyner II, RSM Team Leader 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 Signature Date TABLE OF CONTENTS 1.0 BASIC INFORMATION 1 2.0 PRODUCTION 2 3.0 EVALUATED / IMPLEMENTED TECHNOLOGIES AND APPROACHES 5 4.0 TECHNOLOGIES / APPROACHES CONSIDERED FOR 2021 AND BEYOND 7 4.1 Bypass Salting / No Fermentation Process 7 4.2 Desalt Process Improvements 7 4.3 Brine Reclaim Process Improvement - 5-gallon Pail Line 7 4.4 Wastewater Treatment Process Improvements 7 4.5 Pickle Packers International (PPI) 8 4.6 Treatment Technologies 8 5.0 WASTE REDUCTION 9 TABLES Table 1 Annual Production Units and Chloride to Production Ratio (1996-2020) 3 Table 2 Comparison of All Data (2005 — 2020) 4 Table 3 Monthly Chloride Discharge 2020 10 Table 4 Annual Average Stream Chloride Levels 1997-2020 (mg/L) 11 Chart 1 Chart 2 Chart 3 Chart 4 Chart 5 Chart 6 CHARTS Average Chloride Discharge Annual Production Chloride Discharged (Ibs/equivalent unit) Chloride Limits Average Instream Chloride Concentrations Annual Chloride Discharge 1996-2020 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 1.0 BASIC INFORMATION Bay Valley Foods, LLC — Faison, NC (BVF), remains committed to continue efforts to maintain the downward trend in chloride discharges from its production facility. Through emphasis on its comprehensive pollution prevention, advanced process control and automation aimed at reducing brine loss, replacement of inefficient equipment, and ongoing efforts in the identification and implementation of new and innovative reduction opportunities, BVF maintains its focus on the reduction of chlorides from its waste stream (Chart 1). BVF will continue to investigate and monitor technological advances that may have potential application to the pickle processing industry and supports research efforts in this area through its membership in professional trade organizations such as Pickle Packers International. BVF is willing to implement cost-effective chloride removal technologies and pollution reduction measures that can be proven effective and not compromise or impair finished product quality and/or characteristics. 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 1 2.0 PRODUCTION BVF uses an established formula whereby all production types, in all facilities, are normalized. The unit of measure is referred to as an "Equivalent Production Unit" and allows for a fair and equal comparison of differing sized containers from a 10-ounce jar to 5-gallon bucket. The Equivalent Production Unit (EPU) brings all production to a case equivalent volume and enables a fair comparison of production between facilities and production years and provides a balanced method to evaluate performance. The Faison, NC facility production requirements increased annually between the benchmark year of 1996 through 2006, at which time production peaked at 9.04 million EPU (Tables 1 and 2). Since 2006, the trend indicates a reduction in production throughput (Chart 2). The 2020 production volume was 4.575 million EPU, a 1.6% decrease from the 2019 volume (4.835 million EPU) (Table 1). The 2020 average ratio of chloride discharged in pounds per EPU (0.42) is above the 1996 — 2020 average ratio (0.31) and the 2015 - 2020 five-year average ratio (0.29) (Table 1). The increase in chloride discharge per EPU in 2020 is due to the production of a new product that requires fermenting. Due to the ongoing commitment from facility leadership, the pounds of chloride discharged per EPU continue to show a long-term downward trend (Chart 3). 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 2 Table 1: Annual Production Units and Chloride to Production Ratio (1996-2020) Production Year ■ Production Equivalent Units (millions) Chloride to Units Produced Ratio 1996 5.74 0.51 1997 NA NA 1998 NA NA 1999 7.09 0.37 2000 7.28 0.38 2001 7.59 0.31 2002 7.84 0.28 2003 8.52 0.37 2004 8.75 0.31 2005 7.86 0.33 2006 9.04 0.35 2007 8.98 0.40 2008 8.57 0.38 2009 8.82 0.35 2010 8.23 0.39 2011 7.85 0.25 2012 7.26 0.20 2013 6.82 0.19 2014 6.6 0.21 2015 7.01 0.17 2016 6.84 0.22 2017 5.89 0.26 2018 5.49 0.34 2019 4.83 0.19 2020 4.76 0.42 Average 1996-2020 7.289 0.31 Average 2015-2020 5.803 0.27 2020 Annual Chloride Reduction Report Bay Valley Foods, LC - Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 3 0 N 0 N 0 O 0 0 0 0 VI D. 0 N N H o rsi O N V O m 4,757,562 N V o 3,348,508 NA I O u? m co nl O o m o o w o lull co V rn o N CO N Q Z 0 rn o 01 CO ul o Ol co V Oi to co V o lO co V isi V ^o O V m N Ol m rci m N cp — I -- I-- l0 co ^ LO to N to O m co to v lfl lfl 01 0 o co is,to to o Z Ol N v .— to n V O 01 N— Ol V to 0 r r m co lO N N o < Z r r m co — of n? O1 lfl N V N lO o o N V co N N— N lO N 0 I-S N� O Q Z lfl M m m m rv1 to nl r m O V M V CO lfl l0 0 lO O Z r V V lfl N m m 01 O m _ O N V r m h N N lmp co 6' O o Z Z t 0 0 O ui O co M O o ONl O l�o V is, C is, N I-- ci Z to N.: Ol 0 0 ni O M 01 O N O1 to m V m V c0 r is,N O Z N m Is;Ol — 0 0 O co m is, rsl O co o-,m m m cc, to lfl N N O m m o Q Z N-:O I— 0 O ON O V m o N O 01 ro 0rsl 01 lfl 01 c0 l O Z co I— o 0 0 O rri - V O is, O in N i, ci is, N M 0 0 0 rsi co 01 0 O Q Z m � m 0 0 0 to N o to O co co co M 0 m 01 co co co 0 O 0 Z Z o 0 0 0 nl t to V 0 0 co 01 co 0 0 ill of o Oi i , re-, O Q Z "'1 0 0 O of ONi V in O n — h N o m N CO m m O Q Z N rn — 0 a V O Data Description "I Annual Chloride Discharge (Ibs) Annual Production (equivalent units) Chloride Discharge Per Equivalent Unit (Ibs/equivalent unit) Annual NaCI and CaCI Use (Ibs) Annual Water Use (MG) Annual NaCI & CaCI Purchases (Ibs) Salt Use per Equivalent Unit (Ibs/equivalent unit) 3.0 EVALUATED / IMPLEMENTED TECHNOLOGIES AND APPROACHES Summary of Chloride Reduction Strategies Implemented and / or Evaluated at Faison, NC • 1982 through 1990 — Replaced all wood fermentation tanks with fiberglass or plastic • 1982 through 1994 — Salt Use Reduction in Brining - % salt reduced from 15.8% to 6.3% salt (Substitute calcium chloride and acetic acid in brine prep) • 1987 to 1989 — Recycle Brine — Currently recycle 100% of brine • 1988 — Desalting Operation Moved to Brine Yard • 1991 — Enhanced Automation of 5-Gallon Production Line • 1991 — Enhanced Automation of Major Customer Brine System • 1992 — Replace Open -Top Blancher with Rotary Blancher • 1992 — Enhanced Bulk Product Handling Processes • 1993 — Upgrade Brine -making Station • 1993 — Replace Brine Yard Pickle Pump • 1994 — Install Titanium Heat Exchanger — Brine Recycling/Pasteurization Process • 2002- Increase Brine Reclaim • 2003, 2004, 2005, 2006 — Evaluate Use of De -Salt Water for Brining and/or Product Fluming • 2003, 2004, 2005, 2006 — Evaluate Use of De -Salt Water for Subsequent De -Salting Operations • 2003, 2004 — Evaluate Recovery of Bottom 2-inches of Concentrated Brine Left in Fermentation Tanks After Cleaning • 2004 — Install De -Salt Flume Conveyor • 2004 — Evaluate De -Salt Brine Filtering for Possible Reuse • 2004, 2005 — Evaluate De -Salting through the Lyco Blancher (Continuous Process vs. Batch Process) • 2004, 2005 — Evaluate Rapid De -Salt Process • 2005, 2006 — Evaluate Improvement in Cover Brine Recovery/Blow Lines • 2005 — Evaluate New De -Salting Operation Located in Tank Yard • 2005 — Install WW Sludge Filter Press and Clean Sludge from WW Treatment Ponds • 2005, 2006, 2007, 2008 — Evaluate In -Line De -Salting • 2005 — Implemented By -Pass Salting / No Fermentation Process • 2005 (2006, 2007, 2008 2009) — Begin 4-Phase Storm Water Management Project • 2007, 2008 — Improvements to Cover Brine Efficiency & Recovery Line 1 and 2 • 2008 — Implemented Enhanced Relish Desalting Control • 2009 — Implemented Replace Pickle Conveyor Pump • 2009 — Implemented Upgrade Desalting Operation by Installing Four Additional De -Salt Tanks • 2011 — Implemented a project to remove excess biomass from Pond 1 of its wastewater treatment system. 1500 tons of biomass was dewatered and removed at a cost of $143,000. • 2012 — Continued the removal process of excess biomass from Pond 1 with an additional removal and dewatering of 3000 ton at a cost of $249,000. 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 5 ♦ 2014 - Continued the removal process of excess biomass from Pond 1 with an additional removal and dewatering of 3643 ton at a cost of $368,000. ♦ 2016 - Implemented removal process of excess biomass from Pond 2 with removal and dewatering of 3727 tons at a cost of $230,000. ♦ 2016 — Implemented removal and replacement of Pond 2 liner and begin construction and lining of Pond 3 at a cost of $500,000. ♦ 2016 — Evaluate Reverse Osmosis and Electrodialysis/Electrodialysis Reversal to Reduce Chloride at End -of -Pipe. Neither technology was considered feasible due to cost considerations. ♦ 2017 — Completed the excess biomass removal from Pond 3 with removal and dewatering of 1,963 tons at a cost of $336,000. ♦ 2017 — Completed installing the new liner at Pond 3 on April 1, 2017 at a cost of $100,000 ♦ 2018 — Completed lining Pond 1. Sludge removal cost totaled $285,000. The three ponds have been relined. 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 6 4.0 TECHNOLOGIES / APPROACHES CONSIDERED FOR 2021 AND BEYOND Many projects, programs, process changes and chloride reduction strategies implemented in the past continued to be utilized into 2021 as described in the following sections. 4.1 Bypass Salting / No Fermentation Process The proprietary "No Fermentation" process continues to be a significant process improvement and chloride reduction strategy and will be considered for all future production opportunities where applicable. 4.2 Desalt Process Improvements The Faison facility added four portable de -salt tanks for product de -salting. The de -salting process must be accomplished quickly to support the production schedule, which can result in over de -salting of the product necessitating the re -addition of salt. The result is excess water use, increased salt use and ultimately additional chloride discharges. The four portable de -salt tanks enabled the facility to extend the duration of the de -salt process, which provided improved process control. Status: Successful process improvements were made to the de -salt process in 2009. Cost Associated with Improvements - $350,000. 4.3 Brine Reclaim Process Improvement - 5-gallon Pail Line The installation of catch pans, filter screens, and a brine reclaim tank on the 5-gallon pail line allows for the capture of overflow brine and eventual reuse, rather than discharged as high chloride concentrated wastewater. Status: Successful improvements were made to the brine reclaim system on the 5-gallon pail processing line in 2009. Cost Associated with Improvements - $4,500. 4.4 Wastewater Treatment Process Improvements Excess biomass accumulation in Pond 3 was removed and the pond was relined. This project was completed in April 2017. In 2017, BVF removed biomass accumulation from Pond 1 and began the 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 7 process to re -line Pond 1. Sludge removal was completed in March 2018, and the liner replacement was completed. Pond 1 aerators were re -wired, and the pond was returned to normal operations on May 1,2018. Status: Successful improvements were made to the wastewater ponds. Sludge removal costs - $285,000. 4.5 Pickle Packers International (PPI) BVF is a member of, and continues to participate in, the Pickle Packers International organization. Through participation in this organization, BVF remains current on new processing technologies which may include reduced salt use, and wastewater treatment strategies others in the pickle processing industry may have implemented that result in reduced chlorides in wastewater discharges. 4.6 Treatment Technologies Ramboll Environ prepared a Chloride Removal Technology Evaluation Report dated January 12, 2017. The report identified several technologies potentially applicable to the BVF facility. The technologies included reverse osmosis, electrodialysis / electrodialysis reversal, chemical precipitation, product substitution, flow augmentation, and residuals management. BVF is committed to investigating and evaluating any new treatment technology based on technical applicability and feasibility. 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 8 5.0 WASTE REDUCTION The ongoing waste reduction efforts at the Facility will continue through 2021. The facility has formed a cross -functional Pollution Prevention Team (Team) that meets on a regular basis to discuss and evaluate waste generation and chloride reduction opportunities. A comprehensive pollution prevention program is in place which includes educating employees regarding waste best management practices and the importance of identifying strategies that can reduce chloride discharges. Chloride reduction is a primary focus of the Team along with water conservation, efficient utilization of energy, and waste generation. In addition, the Team considers maintenance practices and other protocols that may result in brine loss. Finally, the Team is continually evaluating processes for redesign consideration with respect to improved efficiency and chloride discharge reduction opportunities. In combination with waste reduction and pollution prevention efforts, BVF continues to focus on preventive maintenance programs and giving a priority assignment to any maintenance work order involving process equipment that could result in increased discharge of chlorides. These activities along with employee training help foster and expand a work ethic focused on waste reduction as well as process improvements. The maximum daily discharge for each month in 2020 was below the daily maximum limit and the average monthly discharge was below the monthly average limit (Table 3 and Chart 4). Upstream chloride concentrations represent background values. An anomalous peak in downstream chloride concentrations observed in 2007 was attributed to low stream flow conditions throughout the year, a result of drought conditions. Linear regressions performed on chloride stream concentrations indicate decreasing trends (negative slopes) in Downstream Points #1 and #3, and an increasing trend (slightly positive slope) in Downstream Point #2 (Chart 5). The average annual chloride discharge decreased from 2007 to 2020 (Table 4, Chart 6). From 2015 to 2020, chloride concentrations have fluctuated, but have remained below the 2007 concentrations. The provided charts demonstrate that waste reduction efforts at the BVF facility are effective. 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 9 Table 3: Monthly Chloride Discharge 2020 Current Chloride Discharge Monthly Average = 13,476 lb/day Limits: Daily Maximums= 19,120 lb/day Chloride Discharge (Ib/day) Month Max Min Avg. January 5719 1387 3487 February 8109 787 4812 March 7081 2210 4027 April 9434 931 4958 May 8166 3963 5560 June 8714 3298 5717 July 12762 2712 8708 August 14509 8425 10442 September 9693 308 3948 October 9045 2158 5106 November 8629 1678 4399 December 7367 2269 3986 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 10 Table 4: Annual Average Stream Chloride Levels 1997-2020 (mg/L) Year Upstream Downstream 1 Downstream 2 Downstream 3 1997 9.1 771 249 132 1998 21 963 271 133 1999 23 616 132 92 2000 22 601 91 66 2001 25 753 123 102 2002 30 790 290 170 2003 20 354 81 60 2004 22 424 52 45 2005 24 768 121 91 2006 23 565 99 74 2007 37 2129 516 249 2008 26 1284 174 149 2009 38 1133 194 140 2010 33 974 314 125 2011 29 900 436 130 2012 64 731 167 159 2013 27 587 98 79 2014 25 310 94 61 2015 20 320 140 70 2016 24 402 252 60 2017 19 482 330 76 2018 23 244 114 53 2019 23 526 214 77 2020 18 243 106 44 2020 Annual Chloride Reduction Report Bay Valley Foods, LC — Faison, North Carolina NPDES Permit No. NC0001970 DAA Project No. 2100309 March 15, 2021 11 CHARTS Chart #1 Average Chloride Discharge (Ibs/day) O c c O O , c 0 0 01 4 •D > i 0 3 cu cr O. a) V To o c (I) c c Q O .E CO N- CO LC) CO N 1996 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019 2020 Chloride Discharged (Ibs/equivalent unit) O 1996 2001 Average Daily Discharge Maximum Daily Discharge c 0 X 2 Monthly Avg Li O O O O O O O O O O O O O O O O O O O LC) O LC') O LC) CO N N r r November December O Q O U 0 September 0 Q U Average Instream Chloride Concentration (Ibs per day) 1 \N y =-1.8233x + 125.26 y = 1.4855x + 170.32 y =-16.004x + 910.26 ° ° d ° P a 6 1 - Upstream (Background) - Downstream Point #1 Downstream Point #2 Downstream Point #3 • Linear (Downstream Point #1) • Linear (Downstream Point #2) Linear (Downstream Point #3) ° 1 a ° 9° I ® I I ° °I I ° 01 , I a°1 EI 1 1 ° Io O I I ° PI J I® 9° °i ° cl 1 I® 0 0 N 0 0 r 0 0 0 0 M 0 0 0 0 0 M 1-0 N 0 0 0 0 0 N 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019 2020