Francis de los Reyes III | |
---|---|
Born | Francis Lajara de los Reyes III |
Occupation(s) | Environmental engineer, academic and global sanitation advocate |
Academic background | |
Education | B.S., Agricultural Engineering M.S., Civil Engineering Ph.D., Environmental Engineering |
Alma mater | University of Philippines at Los Banos Iowa State University University of Illinois Urbana-Champaign |
Academic work | |
Institutions | University of the Philippines at Los Baños North Carolina State University |
Francis Lajara de los Reyes III is a Filipino-American environmental engineer,academic,and global sanitation advocate. He is the Glenn E. and Phyllis J. Futrell Distinguished Professor and Alumni Distinguished Undergraduate Professor in the Department of Civil,Construction,and Environmental Engineering at North Carolina State University. [1]
De los Reyes is most known for his research that combines modeling,bioreactor experiments,and molecular microbial ecology to address problems in environmental biotechnology and engineering,and his public outreach for improving sanitation in developing countries. His works have been published in academic journals,including Environmental Science &Technology and Applied and Environmental Microbiology . [2] Moreover,he is the recipient of the 2022 Rudolfs Industrial Waste Management Medal from the Water Environment Federation. [3]
De los Reyes completed his B.S. in Agricultural Engineering in 1990 from the University of Philippines at Los Baños followed by an M.S. in Civil Engineering in 1994 from Iowa State University. Later in 2000,he obtained a Ph.D. in Environmental Engineering from the University of Illinois Urbana-Champaign. [1]
De los Reyes began his academic career at the University of the Philippines at Los Baños,where he held an instructor appointment in the Department of Land and Water Resources Engineering from 1990 to 1992. After graduate school,he joined North Carolina State University in 2000,initially as an assistant professor. He has also served as an adjunct professor at the University of the Philippines at Los Baños since 2010. Additionally,he has been an associate faculty member in the Department of Microbiology at North Carolina State University since 2004 and a professor in the Department of Civil,Construction,and Environmental Engineering since 2012. Since 2022,he has held the Glenn E. and Phyllis J. Futrell Distinguished Professorship at the same institution. [1]
De los Reyes is a TED Fellow [4] and WEF Fellow as well as a Board Certified Environmental Engineering Member of the American Academy of Environmental Engineers and Scientists. He was elected as a corresponding member of the National Academy of Science and Technology,Philippines (NAST PHL) for his contributions to microbial ecology,biotechnology,and environmental engineering,particularly in the Philippines. Moreover,he is an elected member of the Philippine-American Academy of Science and Engineering, [5] where he has held leadership roles such as chair of the board and president. He also served as the founding vice president of the Filipino-American Performing Artists of North Carolina,an organization promoting Filipino culture through the arts. Additionally,he has served on the editorial boards of several academic journals,including Transactions NAST Philippines and ACS ES&T Engineering. [6]
De los Reyes is Chair of the Board of Gawad Kalinga USA. [7]
De los Reyes was part of the team that developed the vomit machine,a tool designed to study the transmission of norovirus. This invention demonstrated the airborne spread of norovirus. Furthermore,this invention was covered by media,with news articles being published in NBC News,Huffington Post and Washington Post. [8] [9] [10] Furthermore,he has been an advocate for better sanitation access in underserved communities. [11] [12]
De los Reyes has worked on various topics at the intersections of waste and wastewater conversion to energy,microbial ecology,and global sanitation technologies. In 1997,he authored a paper that described the development and validation of specific oligonucleotide probes for identifying and quantifying filamentous bacteria associated with foaming in activated sludge systems,highlighting their utility in monitoring microbial populations responsible for operational issues. [13] While investigating the role of Gordonia spp and Gordonia amarae in foam formation and stability in activated sludge systems,his 2002 study identified critical concentration thresholds and their correlation with temperature and foaming events through experimental and real-world analyses. [14] Through his 2007 study,he developed and validated sensitive SYBR green Q-PCR assays for detecting and quantifying Bacillus atrophaeus and Serratia marcescens,surrogates for biological warfare agents,in synthetic building debris and leachate,ensuring specificity and effective spore lysis methods. [15]
De los Reyes' 2011 work explored methanogenesis initiation in landfill waste decomposition,emphasizing Methanosarcina barkeri's importance in low pH environments. It revealed the absence of pH-neutral niches pre-methanogenesis,subsequent pH-neutral zones in high-moisture areas with M. barkeri,and spatial variability within landfill reactors. [16] In the same year,he investigated the formation mechanisms of fats,oil,and grease (FOG) deposits in sanitary sewer lines,proposing a process involving the aggregation of excess calcium and saponification reactions with free fatty acids based on laboratory experiments and analysis of collected deposits. [17] Subsequently,his 2012 paper explored the potential benefits and challenges of co-digesting fats,oils,and grease (FOG) with municipal biosolids in anaerobic digesters at wastewater treatment facilities,aimed at increasing biogas production while addressing issues such as inhibition of bacteria and system blockages. [18] Furthermore,his 2013 study on anaerobic co-digestion of grease interceptor waste with biosolids showed the highest yield of methane to date. [19]
Through his 2017 study,De los Reyes provided a thorough review of the challenges posed by fat,oil,and grease (FOG) in sewer systems,exploring the formation process of FOG deposits,sources of FOG components,potential solutions,implications for sewer maintenance,and future research directions. [20] He also led the development of the Flexcrevator and Excrevator,auger-based technologies for emptying pit latrines that have a lot of trash. The mechanized approach made pit emptying more hygienic,safer,and faster. [21] [22] For this technology,he received the Patents for Humanity Award from the US Patent Office in 2020 and the RELX Environmental Challenge Award in 2018. [23] More recently in 2021,he was part of a team that explored the potential of wastewater surveillance as a complementary tool for monitoring and responding to the COVID-19 pandemic,emphasizing advancements in detection methods,correlation with reported cases,and the need for effective communication between researchers and public health responders. [24]
Waste management or waste disposal includes the processes and actions required to manage waste from its inception to its final disposal. This includes the collection,transport,treatment,and disposal of waste,together with monitoring and regulation of the waste management process and waste-related laws,technologies,and economic mechanisms.
Anaerobic respiration is respiration using electron acceptors other than molecular oxygen (O2). Although oxygen is not the final electron acceptor,the process still uses a respiratory electron transport chain.
Wastewater treatment is a process which removes and eliminates contaminants from wastewater. It thus converts it into an effluent that can be returned to the water cycle. Once back in the water cycle,the effluent creates an acceptable impact on the environment. It is also possible to reuse it. This process is called water reclamation. The treatment process takes place in a wastewater treatment plant. There are several kinds of wastewater which are treated at the appropriate type of wastewater treatment plant. For domestic wastewater the treatment plant is called a Sewage Treatment. Municipal wastewater or sewage are other names for domestic wastewater. For industrial wastewater,treatment takes place in a separate Industrial wastewater treatment,or in a sewage treatment plant. In the latter case it usually follows pre-treatment. Further types of wastewater treatment plants include Agricultural wastewater treatment and leachate treatment plants.
Waste stabilization ponds are ponds designed and built for wastewater treatment to reduce the organic content and remove pathogens from wastewater. They are man-made depressions confined by earthen structures. Wastewater or "influent" enters on one side of the waste stabilization pond and exits on the other side as "effluent",after spending several days in the pond,during which treatment processes take place.
Anaerobic digestion is a sequence of processes by which microorganisms break down biodegradable material in the absence of oxygen. The process is used for industrial or domestic purposes to manage waste or to produce fuels. Much of the fermentation used industrially to produce food and drink products,as well as home fermentation,uses anaerobic digestion.
Industrial wastewater treatment describes the processes used for treating wastewater that is produced by industries as an undesirable by-product. After treatment,the treated industrial wastewater may be reused or released to a sanitary sewer or to a surface water in the environment. Some industrial facilities generate wastewater that can be treated in sewage treatment plants. Most industrial processes,such as petroleum refineries,chemical and petrochemical plants have their own specialized facilities to treat their wastewaters so that the pollutant concentrations in the treated wastewater comply with the regulations regarding disposal of wastewaters into sewers or into rivers,lakes or oceans. This applies to industries that generate wastewater with high concentrations of organic matter,toxic pollutants or nutrients such as ammonia. Some industries install a pre-treatment system to remove some pollutants,and then discharge the partially treated wastewater to the municipal sewer system.
Articles related to waste management include:
An anaerobic lagoon or manure lagoon is a man-made outdoor earthen basin filled with animal waste that undergoes anaerobic respiration as part of a system designed to manage and treat refuse created by concentrated animal feeding operations (CAFOs). Anaerobic lagoons are created from a manure slurry,which is washed out from underneath the animal pens and then piped into the lagoon. Sometimes the slurry is placed in an intermediate holding tank under or next to the barns before it is deposited in a lagoon. Once in the lagoon,the manure settles into two layers:a solid or sludge layer and a liquid layer. The manure then undergoes the process of anaerobic respiration,whereby the volatile organic compounds are converted into carbon dioxide and methane. Anaerobic lagoons are usually used to pretreat high strength industrial wastewaters and municipal wastewaters. This allows for preliminary sedimentation of suspended solids as a pretreatment process.
Upflow anaerobic sludge blanket (UASB) technology,normally referred to as UASB reactor,is a form of anaerobic digester that is used for wastewater treatment.
Secondary treatment is the removal of biodegradable organic matter from sewage or similar kinds of wastewater. The aim is to achieve a certain degree of effluent quality in a sewage treatment plant suitable for the intended disposal or reuse option. A "primary treatment" step often precedes secondary treatment,whereby physical phase separation is used to remove settleable solids. During secondary treatment,biological processes are used to remove dissolved and suspended organic matter measured as biochemical oxygen demand (BOD). These processes are performed by microorganisms in a managed aerobic or anaerobic process depending on the treatment technology. Bacteria and protozoa consume biodegradable soluble organic contaminants while reproducing to form cells of biological solids. Secondary treatment is widely used in sewage treatment and is also applicable to many agricultural and industrial wastewaters.
Sewage sludge treatment describes the processes used to manage and dispose of sewage sludge produced during sewage treatment. Sludge treatment is focused on reducing sludge weight and volume to reduce transportation and disposal costs,and on reducing potential health risks of disposal options. Water removal is the primary means of weight and volume reduction,while pathogen destruction is frequently accomplished through heating during thermophilic digestion,composting,or incineration. The choice of a sludge treatment method depends on the volume of sludge generated,and comparison of treatment costs required for available disposal options. Air-drying and composting may be attractive to rural communities,while limited land availability may make aerobic digestion and mechanical dewatering preferable for cities,and economies of scale may encourage energy recovery alternatives in metropolitan areas.
Biogenic sulfide corrosion is a bacterially mediated process of forming hydrogen sulfide gas and the subsequent conversion to sulfuric acid that attacks concrete and steel within wastewater environments. The hydrogen sulfide gas is biochemically oxidized in the presence of moisture to form sulfuric acid. The effect of sulfuric acid on concrete and steel surfaces exposed to severe wastewater environments can be devastating. In the USA alone,corrosion causes sewer asset losses estimated at $14 billion per year. This cost is expected to increase as the aging infrastructure continues to fail.
A grease trap is a plumbing device designed to intercept most greases and solids before they enter a wastewater disposal system. Common wastewater contains small amounts of oils which enter into septic tanks and treatment facilities to form a floating scum layer. This scum layer is very slowly digested and broken down by microorganisms in the anaerobic digestion process. Large amounts of oil from food preparation in restaurants can overwhelm a septic tank or treatment facility,causing the release of untreated sewage into the environment. High-viscosity fats and cooking grease such as lard solidify when cooled,and can combine with other disposed solids to block drain pipes.
In treatment of sewage one process used is the activated sludge process in which air is passed through a mixture of sewage and old sludge to allow the micro-organisms to break down the organic components of the sewage. Sludge is continually drawn off as new sewage enters the tank and this sludge must then be settled so that the supernatant can be separated to pass on to further stages of treatment.
Aerobic digestion is a process in sewage treatment designed to reduce the volume of sewage sludge and make it suitable for subsequent use. More recently,technology has been developed that allows the treatment and reduction of other organic waste,such as food,cardboard and horticultural waste. It is a bacterial process occurring in the presence of oxygen. Bacteria rapidly consume organic matter and convert it into carbon dioxide,water and a range of lower molecular weight organic compounds. As there is no new supply of organic material from sewage,the activated sludge biota begin to die and are used as food by saprotrophic bacteria. This stage of the process is known as endogenous respiration and it is process that reduces the solid concentration in the sludge.
Sewage treatment is a type of wastewater treatment which aims to remove contaminants from sewage to produce an effluent that is suitable to discharge to the surrounding environment or an intended reuse application,thereby preventing water pollution from raw sewage discharges. Sewage contains wastewater from households and businesses and possibly pre-treated industrial wastewater. There are a high number of sewage treatment processes to choose from. These can range from decentralized systems to large centralized systems involving a network of pipes and pump stations which convey the sewage to a treatment plant. For cities that have a combined sewer,the sewers will also carry urban runoff (stormwater) to the sewage treatment plant. Sewage treatment often involves two main stages,called primary and secondary treatment,while advanced treatment also incorporates a tertiary treatment stage with polishing processes and nutrient removal. Secondary treatment can reduce organic matter from sewage, using aerobic or anaerobic biological processes. A so-called quarternary treatment step can also be added for the removal of organic micropollutants,such as pharmaceuticals. This has been implemented in full-scale for example in Sweden.
Facultative lagoons are a type of waste stabilization pond used for biological treatment of industrial and domestic wastewater. Sewage or organic waste from food or fiber processing may be catabolized in a system of constructed ponds where adequate space is available to provide an average waste retention time exceeding a month. A series of ponds prevents mixing of untreated waste with treated wastewater and allows better control of waste residence time for uniform treatment efficiency.
Resource recovery is using wastes as an input material to create valuable products as new outputs. The aim is to reduce the amount of waste generated,thereby reducing the need for landfill space,and optimising the values created from waste. Resource recovery delays the need to use raw materials in the manufacturing process. Materials found in municipal solid waste,construction and demolition waste,commercial waste and industrial wastes can be used to recover resources for the manufacturing of new materials and products. Plastic,paper,aluminium,glass and metal are examples of where value can be found in waste.
Fecal sludge management (FSM) is the storage,collection,transport,treatment and safe end use or disposal of fecal sludge. Together,the collection,transport,treatment and end use of fecal sludge constitute the "value chain" or "service chain" of fecal sludge management. Fecal sludge is defined very broadly as what accumulates in onsite sanitation systems and specifically is not transported through a sewer. It is composed of human excreta,but also anything else that may go into an onsite containment technology,such as flushwater,cleansing materials,menstrual hygiene products,grey water,and solid waste. Fecal sludge that is removed from septic tanks is called septage.