Showing posts with label Hazardous. Show all posts
Showing posts with label Hazardous. Show all posts

Tuesday, January 24, 2012

Dynatec Provides MBR System for Hazardous Landfill

The Problem


A hazardous waste landfill in Belleville, MI, owned by the Environmental Quality Company had a problem. They needed to develop a treatment process to remove COD, high TDS, heavy metals, phenol, PCB’s, Ammonia, and Molybdenum from the landfill leachate. Current treatment comprised of chlorination and activated carbon treatment was very costly.


Evaluation


The treatment process was challenging. The chemical treatment supplied was based upon the experience batch treating the wastewater and numerous bench scale treatability studies. An MBR process was selected for piloting because it was the best option to nitrify, reduce the high COD and phenol and overcome the potentially toxic conditions. Dynatec was engaged to supply a pilot treatment plant to be used as an investigative tool for the design of the full scale treatment process. The pilot operation phase of the project lasted almost 3 years, where problems were identified and solutions found.


Some unique challenges offered by this application were:


Foaming - Toxicity from the metals, phenol , and other unidentified substances


Mixed Liquor conditioning


Biological temperature sensitivity


Sensitive nitrification process


Difficult chemical precipitation of metals


Small footprint required


Dynatec was engaged to supply and install the full scale system because of Dynatec’s experience with the treatment technologies employed, their familiarity with the project, and the requirement for a high rate MBR process operating at high MLSS.


The Solution


Dynatec provided and installed a system that included a stainless steel insulated covered bioreactor with both heating and cooling capabilities to control temperature within a range suitable for achieving the treatment goals. To solve the foaming problem, a combination of jet aeration, defoamer, DO control, and concentrate return splash plates were employed along with an emergency potable water spray to prevent foam-over.


The membrane filtration equipment was designed to make efficient use of a small existing building that houses the membranes, controls, dewatering and other equipment.


The process includes chemical / physical treatment of the leachate both before and after the MBR. The post MBR chemical precipitation is for Molybdenum. The MBR removes compounds that were found to interfere with the precipitation process. The treated water is discharged to sanitary sewer.


A sludge tank receives the solids from both clarifiers of the pre and post chemical treatment systems as well as the WAS. Additional iron and lime is added and mixed in the sludge tank prior to feed to the filter press for dewatering. The solids are discharged within the landfill.


The Process


The process design consists of the following:

The hazardous wastewater is pretreated for removal of CN, Cr, Cu, Pb, Ni and Zn.The hazardous wastewater is mixed with non hazardous wastewater in a 500,000 gallon EQ tank to help make nitrification work. Approximately 65% of the wastewater discharged to the EQ tank is hazardous WW and 35% is non haz.The WW in the EQ tank is sent to the MBR for treatment for reduction in phenol ammonia nitrogen and COD.The MBR permeate is post treated for removal of molybdenum. The moly is apparently organically bound and does not precipitate adequately in the pretreatment.Sludge from the metals precipitation is mixed with WAS and dewatered in a filter press.

Operation


The system started up in March of 2010. As expected, the activated sludge took less than two months of conditioning before effective treatment was achieved due to the information and knowledge that was gained during piloting. A special bacterial culture was added to promote nitrification, which improved performance.


The COD  of the hazardous wastewater varies significantly, typical values observed have been between 5,000 mg/L and 12,000 mg/L. After blending with non hazardous leachate the COD is typically in the range between 3,000 mg/l and 6,000 mg/l.


The system operator is able to adjust conditions as needed. The system is currently operating at high mixed liquor concentration, an average of 24,000 mg/l. The jet aeration system makes operation at this level possible. Temperature ranges from a low of 25’C in the winter to 36’C in the summer. A natural gas fired heater heats the leachate in the winter in the recirculating loop between the bioreactor and the UF. The heater runs very little as the tank is covered and insulated. The system also has the ability to cool the mixed liquor as the temperature approaches 38’C to prevent thermophilic conditions from developing.


The continuous addition of defoamer is necessary. The concentrate return hits splash plates in the reactor to create a spray of sorts to help depress foam. There is also a fresh water spray available for use that rings the top inside of the reactor.


After startup, the system is operating as designed. The operators have used the emergency potable water spray to prevent foam-over of the bioreactor a couple times, with no other major issues. The system is exceeding expectations. Phenol in the effluent is typically below 0. 1 mg/L and metals removal is consistently below discharge requirements and below toxicity levels required to protect the biological process.


Conclusion


This is a very tough job. The complete and comprehensive system that Dynatec provided made this a success, and many lessons were learned for future projects. Dynatec was the right choice for this difficult MBR application. The many years of experience Dynatec has applying membranes to wastewater has enabled it to design and provide systems that perform in even the most difficult applications.


The system payback is expected to be very short. The system is meeting all its treatment objectives.


View the original article here

Monday, December 06, 2010

A Scheme for the analysis of pollutants in groundwater and leachates contaminated by hazardous chemicals

Sanitary landfills are the most widely utilized method of solid waste disposal around the world. With increased use and public awareness of this method of disposal, there is much concern with respect to the pollution potential of the landfill leachate. Depending on the composition and extent of decomposition of the refuse and hydrological factors, the leachate may become highly contaminated. As leachate migrates away from a landfill, it may cause serious pollution to the groundwater aquifer as well as adjacent surface waters.


There is growing concern about surface and groundwater pollution from leachate. Better understanding and prediction of leachate generation, containment, and treatment are needed. This book contains a literature review of various methodologies that have been developed for prediction, generation, characterization, containment, control, and treatment of leachate from sanitary landfills. The contents of this book are divided into nine chapters. Each chapter contains theory and definition of the important design parameters, literature review, example calculations, and references. Chapter 1 is devoted to basic facts of solid waste problems current status and future trends towards waste reduction and recycling.


Chapter 2 provides a general overview of municipal solid waste generation, collection, transport, resource recovery and reuse, and disposal options. The current status of sanitary landfill design and operation, problems associated with the landfilling, and future trends are presented in Chapter 3. Methods of enhanced stabilization, recycling landfill space, methane recovery, and above grade landfilling, and closure and post closure care of completed landfills are also discussed in detail.


Chapter 4 provides a general overview of Subtitle D regulations and its impact upon sanitary landfilling practices. Chapter 5 is devoted entirely to moisture routing and leachate generation mechanisms. Examples of calculation procedure for determining the leachate quantity produced at a landfill are presented. Chapter 6 is devoted to chemical characterization of leachate that changes over the life of the fill. Both theoretical and experimental results are provided to estimate the leachate quality. Chapter 7 provides leachate attenuation processes and mechanisms.


Chapter 8 is devoted to leachate collection systems. Natural soil sealants, admixed materials and synthetic membranes, their effectiveness, and methods of installation and economics are fully discussed. Chapter 9 provides a detailed review of leachate treatment methodology. Kinetic coefficients and treatment plant design considerations are summarized for the sole purpose of assisting con- sultants to design leachate treatment facilities. Leachate treatment case histories and numerous process trains are presented for treating leachate from young landfill. The book also describes how the process train can be changed effectively as leachate quality changes with time.


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Friday, December 03, 2010

Composition of leachates from actual hazardous waste sites (SuDoc EP 1.89/2:600/S 2-87/043)

Treatment of landfill leachate is a challenge specially to the developing countries in the process of protecting their environment due to unaffordability of the available technologies. This study, Advanced oxidation combined with Membrane Bio- reactor (MBR) is an effort to achieve better treatment technique. It focuses on reduced need for infrastructure and smaller foot print of treatment facility by using MBR technology to perform activated sludge process. The subsequent advanced oxidation by ozone facilitates further treatment. Leachate of average age was preteated and fed into a laboratory MBR treatment module. Pretreatment efficiency and the change of MBR efficiency by recirculating the ozonated effluent were studied.

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