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Relevant bibliographies by topics / Landfill leachate

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Academic literature on the topic 'Landfill leachate'

Author: Grafiati

Published: 4 June 2021

Last updated: 15 June 2025

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Journal articles on the topic "Landfill leachate"

1

Warwick, SJ, P. Durany-Fernandez, DJ Sapsford, PJ Cleall, and MJ Harbottle. "Altered chemical evolution in landfill leachate post implementation of biodegradable waste diversion." Waste Management & Research: The Journal for a Sustainable Circular Economy 36, no. 9 (2018): 857–68. http://dx.doi.org/10.1177/0734242x18785723.

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Within the UK implementation of the European Union Landfill Directive (1999) has led to the diversion of biodegradable waste (BW) from municipal solid wastes away from landfills. It has been widely anticipated, but thus far not verified, that the diversion of BW and consequent reduction in BW reaching landfill would lead to a change in the degradation processes occurring within landfills and that this would be reflected in an altered evolution in leachate chemistry compared to pre-Directive landfills. This paper provides evidence based on leachate chemistry from two operational landfills together with calculations of the reduced BW content, that demonstrate the acetogenic phase that characterised pre-Directive landfill leachates is missing and is now more typical of methanogenic phase leachate. The paper demonstrates how data from national datasets and detailed landfill records can be used to constrain likely and upper estimates of the amount of BW going into post-Directive landfills, and the observed change in the evolution of leachate chemistry which has resulted from a decrease in BW content from typical values of BW (pre-Landfill Directive) of 22% to an inferred 12% in the case-study landfills. Data provided here add to the growing literature that estimates the amount of BW in recent post-Directive landfills which importantly allow the quantitative linkage between a decrease in landfilled BW and observed changes in leachate chemistry to be established such that future landfill operators can increase confidence in the effect of Directive implementation on landfill operational parameters.

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Zloch, Jan, Magdalena Daria Vaverková, Dana Adamcová, et al. "Seasonal Changes and Toxic Potency of Landfill Leachate for White Mustard (Sinapis alba L.)." Acta Universitatis Agriculturae et Silviculturae Mendelianae Brunensis 66, no. 1 (2018): 235–42. http://dx.doi.org/10.11118/actaun201866010235.

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Landfills are the most broadly used methods for the disposal of municipal solid waste (MSW). Leachate can be contaminated with pollutants that may pose a threat to the landfill surrounding namely soil, groundwater and surface waters.. Examination of leachate composition is determinative in long-term impact of landfills on the environment and human health. Moreover, it is essential to assess such prior knowledge for prevention of negative outcomes. The evaluation of the seasonal changes of landfill leachate and rainwater composition is presented in this paper. Research samples of leachate and rainwater were collected from February till June of 2017 (still ongoing) and analyzed for pH, electrical conductivity, dissolved oxygen, series of trace elements, Subsequently the test of leachate toxicity for higher plants (Sinapis alba L.) was carried out. Up to now, the results do not indicate significant seasonal difference in landfill leachate composition, however the toxicity tests provided on Sinapis alba L. demonstrate that landfill leachates can present a significant source of contamination. This research can serve practical tools for evaluating quality and risk assessment for landfill leachate.

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Onay, T. T., and F. G. Pohland. "Nitrogen and sulfate attenuation in simulated landfill bioreactors." Water Science and Technology 44, no. 2-3 (2001): 367–72. http://dx.doi.org/10.2166/wst.2001.0791.

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The characteristics of leachate from landfills vary according to site-specific conditions. Leachates from old landfills are often rich in ammonia nitrogen, posing potential adverse environmental impacts in the case of uncontrolled discharge. At landfills where leachate recirculation is practiced, leachate ammonia concentrations may accumulate to higher levels than during the single pass leaching. Using leachate recirculation with system modifications, separate aerobic and anoxic zones for nitrification and both autotrophic and heterotrophic denitrification can be provided. Results from simulated landfill bioreactors indicated that both nitrogenous and sulfur compounds can be attenuated through autotrophic denitrification, and leachate nitrate concentrations of 750 mg/L reduced to less than 1 mg/L by denitrification to nitrogen gas promoting this very common process in a landfill environment results in the reduction of both leachate ammonia and sulfate concentrations.

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Brkanac, Sandra Radić, Valerija Vujčić, Petra Cvjetko, Vid Baković, and Višnja Oreščanin. "Removal of landfill leachate toxicity and genotoxicity by two treatment methods." Archives of Industrial Hygiene and Toxicology 65, no. 1 (2014): 89–99. http://dx.doi.org/10.2478/10004-1254-65-2014-2431.

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Summary Leachates from active and closed municipal solid waste landfills can be a major source of contamination to groundwater and surface waters. In the present study the toxic and genotoxic potential of leachate from an old sanitary landfill prior to and following chemical and electrochemical treatments were assessed using Lemna, Allium, and comet tests. Photosynthetic pigments, malondialdehyde (indicator of lipid peroxidation) and antioxidant enzyme activities were evaluated as additional indicators of toxicity in duckweed. Following duckweed exposure to 25 % dilution of landfill leachate, growth rate and photosynthetic pigments content significantly decreased while lipid peroxidation increased despite stimulation of antioxidative defence mechanisms. Diluted leachate induced DNA strand breaks in duckweed cells as evidenced by the comet assay. Regarding the Allium test, untreated leachate caused inhibition of Allium cepa cell division and induction of mitotic and chromosomal aberrations. Although both water treatments completely reduced genotoxicity of leachate, the electrochemical method was found to be more efficient in removing toxic substances present in landfill leachate and thus more suitable for treating such leachates prior to their discharge into the environment. As landfill leachates pose a risk to human health and environment in general due to their (geno)toxicity, the present study demonstrates that the ecotoxicity/genotoxicity assays should be used in leachate risk assessment together with physicochemical analysis.

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Calic, Natasa, and Mirjana Ristic. "Vinca landfill leachate characteristics prediction by the leaching method." Chemical Industry 60, no. 7-8 (2006): 171–75. http://dx.doi.org/10.2298/hemind0608171c.

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Under the newly implemented waste management policy in European Union countries, sanitary landfilling constitutes the fourth and the least preferred of the alternative management options for the disposal of solid urban wastes. Landfills generate emissions over long periods, often longer than a lifetime. The longest lasting emission is leachate: leachate production and management is now recognized as one of the greatest problems associated with the environmentally sound operation of sanitary landfills. These liquid wastes can cause considerable pollution problems by contacting the surrounding soil, ground or surface waters and, are therefore considered major pollution hazards unless precautionary measures are implemented. Landfill leachate characterization is a critical factor in establishing a corresponding effective management strategy or treatment process. This paper summarizes leachate quality indicators, and investigates the temporal variation of leachate quality from municipal solid waste. The toxicity of leachates from the municipal solid waste landfill "Vinca" in Belgrade, the capital of Serbia, was characterized using toxicity characteristics leaching procedures (TCLP). The "Vinca" landfill was established in 1978 as one of several municipal landfills. Since the 1990-ies the "Vinca" landfill has been the only operating landfill servicing the Belgrade Metropolitan area, the biggest city in Serbia, with 1,576,124 inhabitants in the larger-city area, and 1,273,651 inhabitants in the inner-city area. The total average amount of solid wastes deposited in the landfill is estimated to be 1100 tons/day. The landfill site is not lined and the tributary flows through the centre of the site-in some places directly under the mass of refuse. No consideration has been given to the protection of ground waters, surface runoff or drainage. Local authorities plan to expand the landfill by 0.4 km2 to a total of 1.3 km Chemical analysis was performed on the samples and the temporal variation of several parameters was monitored including pH, COD, chlorides, sulfates, nitrates, ammonia nitrogen, hardness, and heavy metals. The COD and pH were related to the biological activity within the landfill and the results indicated differences between the samples due to waste age. The concentrations of heavy metals, sulfates, nitrates, chlorides and ammonia nitrogen in the leachate were low, indicating their initially low amount in landfilled waste or their flushing with moisture contributing to a reduction in their concentrations.

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Paxéus, N. "Organic compounds in municipal landfill leachates." Water Science and Technology 42, no. 7-8 (2000): 323–33. http://dx.doi.org/10.2166/wst.2000.0585.

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Leachates from three municipal landfills in the Göteborg area of western Sweden were characterised in terms of their content of individual organic compounds. Two of the investigated landfills were still in use during the time of this study. The third landfill was closed down in the mid-seventies. More than 200 individual organic compounds and classes of compounds were identified in the leachate with concentrations ranging from less than one up to several hundred μg/L. Among the compounds common to all three landfills were plasticizers (phthalates, benzenesulfonamides), phosphate esters, substituted phenols, chlorinated phenols, phenolic antioxidants and siloxanes as well as the compounds formed during the degradation of organic wastes (dihydro-dioxin, pyrazines and several sulphur-containing odorous volatiles). Dioxanes and dioxolans found in the leachates have not been previously reported. Compounds originated from previously disposed oil contaminated wastes dominate the leachate from an old closed landfill. Its replacement, a new regional landfill has a leachate dominated by alcohols and ethers. This difference is attributed to regional measures in waste management.

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Wdowczyk, Aleksandra, and Agata Szymańska-Pulikowska. "Differences in the Composition of Leachate from Active and Non-Operational Municipal Waste Landfills in Poland." Water 12, no. 11 (2020): 3129. http://dx.doi.org/10.3390/w12113129.

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Leachate formation is one of the many environmental hazards associated with landfilling. The leachate may migrate from the landfill to surface water and groundwater, posing a potential threat to aquatic ecosystems. Moreover, its harmful effect on human health and life has been proven. Due to the risks that landfill leachates may pose, it is necessary to control the state of the environment in their surroundings. The paper presents an example of the application of selected statistical methods (basic statistics, statistical tests, principal component analysis) to assess the impact of individual pollution indicators on the quality of landfill leachates. The conducted analysis showed the existence of significant differences between the surveyed active (Legnica, Jawor) and non-operational (Wrocław, Bielawa) landfills in Poland. These differences were especially visible in the cases of the following: electric conductivity (EC) (non-operational landfills 1915–5075 μS/cm, active 5093–11,370 μS/cm), concentrations of total Kjeldahl nitrogen (TKN) (non-operational landfills 0.18–294.5 mg N/dm3, active 167.56–907.4 mg N/dm3), chemical oxygen demand (COD), organic nitrogen (ON), ammonium nitrogen (AN), total solids (TS), total dissolved solids (TDS), total suspended solids (TSS), sulfates, chlorides, sodium, potassium, calcium, magnesium and nickel. Selected indicators should help to determine the progress of decomposition processes inside the landfill and the potential impact of leachate on the environment, and should be used in the mandatory monitoring of landfills.

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Wowkonowicz, Paweł, Marta Kijeńska, and Eugeniusz Koda. "Potential environmental risk assessment of di-2-ethylhexyl phthalate emissions from a municipal solid waste landfill leachate." PeerJ 9 (October 1, 2021): e12163. http://dx.doi.org/10.7717/peerj.12163.

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Background In certain countries, including Poland, polyvinyl chloride (PVC) waste, together with di-2-ethylhexyl phthalate (DEHP) contained within (up to 60%), is mostly directed to municipal solid waste (MSW) landfills. From there, over time, it is released from the polymer matrix and can migrate with landfill leachate into the environment. The amount of DEHP placed on the Polish market since the start of industrial production and the prevalent landfilling disposal of PVC waste in Poland, indicate that DEHP pollution can increase risk factors in the future. The objective of this study was to determine the concentrations of DEHP in leachates from a chosen MSW landfill directed to a local sewage treatment plant (STP) and estimate the associated potential risks to the environment. Results DEHP concentrations in leachates ranged from < LOQ to 394.4 µg/L, depending on the sampling year and season. DEHP is a pervasive environmental contaminant present in all investigated landfill leachate samples. The results from The European Union System for the Evaluation of Substances (EUSES) modelling related to DEHP in leachate directed to STP indicated potentially unacceptable risk to freshwater organisms; and birds and mammals feeding on earthworms (where a sewage sludge applications in agriculture take place). The results indicated low risk for other environmental components including local fresh-water sediment, local soil and microorganisms of STP, and freshwater fish-eating birds and mammals. Conclusions Future DEHP emissions may occur after the technical lifetime of the landfill and/or decay its bottom sealing. To avoid contamination, the monitoring of landfills after closure should include DEHP concentrations and last longer than the recommended (inter alia in Poland) 30 years, or until emissions from PVC to leachate are eliminated. More research on leachate of DEHP and its potential risks should be conducted, utilising detailed modelling which can including other landfills and different routes of DEHP emissions in leachates.

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Amini Rad, Hasan, Moslem Salehi Ziri, and Leila Babaei. "Investigation of landfill leachate treatability for reuse in agricultural purposes." Water Practice and Technology 12, no. 1 (2017): 224–33. http://dx.doi.org/10.2166/wpt.2017.011.

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Leachates from landfills are one of the environmental challenges in developing countries, such as Iran that also will face water scarcity in the near future. Landfill leachate management to decrease the negative impact on water resources is indispensable. On the one hand, depending on the age of landfill, high ammonia concentration leachates could be a resource for use in agricultural purposes and on the other, treated leachate can be used as a valuable resource for agronomic irrigation. In order to investigate this hypothesis, landfill leachate was provided from the Sari municipal landfill in the north of Iran (COD = 7,045 mg/l; BOD5/COD = 0.36) and the performance of different combinations of biological, chemical and membrane processes were evaluated according to Iran's Agricultural Water Standard (IAWS). The treatment processes consisted of sequencing batch reactor (SBR), Fenton's process/SBR, and membrane/SBR/Fenton. Results indicated in addition to access IAWS, the treated leachate through Membrane/SBR/Fenton's process could be used as a nitrogen source for agricultural purposes. The removal efficiency of primary parameters, including COD, BOD5, turbidity, and color were 89%, 96%, 99% and 98%, respectively.

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Dolhan, Mimi Malisa, Noor Farahin Bain, and Nur Shuhada Arbaan. "Penghilangan Logam Berat Dari Lindi Tempat Pembuangan Sampah Menggunakan Tanaman Akuatik." JURNAL ILMIAH AGRINECA 25, no. 1 (2025): 31–38. https://doi.org/10.36728/afp.v25i1.4371.

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Landfill leachate, a contaminated liquid produced from rainwater passing through waste materials, presents serious environmental risks by polluting soil and water sources. This study examines the potential of water spinach (WS) (Ipomoea aquatica), water hyacinth (WH) (Eichhornia crassipes), and marsh pennywort (MP) (Hydrocotyle umbellata) to remove heavy metals from landfill leachateIt evaluates levels of heavy metals such as zinc (Zn), copper (Cu), and iron (Fe) to assess the effectiveness of pollutant removal. Leachates from landfills were distributed among four basins over a period of 28 days; (Basin 1 – control, basin 2 – water hyacinth, basin 3 – water spinach, basin 4 – marsh pennywort) and each basin underwent testing with different retention times. The results proved substantial decrease in all of the selected heavy metals (Zn, Cu and Fe) levels after treatment with WH, WS and MP. All the aquatic plants demonstrate an ability to absorb heavy metals, leading to lowered concentrations in the leachate. These findings highlight WH, WS and MP promise as phytoremediation tools for managing landfill leachate contamination that can help to combat pollution and safeguard water resources. This project aims to compare how effectively WS, WH and MP, with various exposure times, can eliminate heavy metals.

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Dissertations / Theses on the topic "Landfill leachate"

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Pouliot, Julie-Marie. "Biological treatment of landfill leachate." Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1999. http://www.collectionscanada.ca/obj/s4/f2/dsk1/tape8/PQDD_0005/MQ42192.pdf.

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Zhao, Renzun. "Management strategy of landfill leachate and landfill gas condensate." Diss., Virginia Tech, 2012. http://hdl.handle.net/10919/77186.

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Studies were conducted to evaluate the impact of landfill leachate discharge on the operation of waste water treatment plants (WWTPs). Two aspects of interferences were found: one is UV quenching substances, which are bio-refractory and able to penetrate the biological treatment processes, consequently interfere the UV disinfection in WWTPs. The other one is organic nitrogen, which can pass the nitrification-denitrification process and contribute to the effluent total nitrogen (TN). Also, treatability study was conducted for landfill gas (LFG) condensate. In a laboratory study, leachate samples were fractionated into humic acids (HA), fulvic acids (FA) and Hydrophilic (Hpi) fractions, the specific UV254 absorbance (SUVA254) of the three fractions follows: HA > FA > Hpi. However, the overall UV254 absorbance of the Hpi fraction was important because there was more hydrophilic organic matter than humic or fulvic acids. It was found that the size distribution of the three fractions follows: HA > FA > Hpi. This indicates that membrane separation following biological treatment is a promising technology for the removal of humic substances from landfill leachates. Leachate samples treated in this manner could usually meet the UV transmittance requirement of the POTWs. Also, nitrogen species in landfill leachates under various stabilization states were investigated. Although the effect of landfill stabilization state on the characteristics of organic matter and ammonia is well documented, there are few investigations into the landfill leachate organic nitrogen under different stabilization stages. Ammonia was found to leach out slower than organic matter and can maintain a constant level within the first a couple of years (< 10 years). The concentration and biodegradability of organic nitrogen were found to decrease with landfill age. A size distribution study showed that most of organic nitrogen in landfill leachates is < 1 kDa. The protein concentration was analyzed and showed a strong correlation with the organic nitrogen. Different slopes of regression curves of untreated and treated leachates indicate that protein is more biodegradable than the other organic nitrogen species in landfill leachates. XAD-8 resin was employed to isolate the hydrophilic fraction of leachate samples, hydrophilic organic nitrogen was found to be more biodegradable/bioavailable than the hydrophobic fractions. Furthermore, biological and physical-chemical treatment methods were applied to a landfill biogas (LFG) condensate to explore the feasible treatment alternatives for organic contaminant and arsenic removal efficiency. Sequencing batch reactor (SBR) showed effectiveness for the degradation of organic matter, even in an environment containing high levels of arsenic. This indicated a relatively low toxicity of organic arsenic as compared to inorganic arsenic. However, for arsenic removal, oxidation-coagulation, including biological oxidation, conventional oxidation and advanced oxidation followed by ferric salt coagulation, and carbon adsorption were not effective for what is believed to be tri-methyl arsenic. Among these, advanced oxidation-coagulation showed the best treatment efficiency (15.1% removal). Only reverse osmosis (RO) could reduce the arsenic concentration to an acceptable level to meet discharge limits. These results implied high stability and low toxicity of organic arsenic.<br>Ph. D.

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3

Zalesny, Jill Annette. "Phytoremediation of landfill leachate using Populus." [Ames, Iowa : Iowa State University], 2007.

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Cheung, Kwai Chung. "Purification of landfill leachate by microalgae." HKBU Institutional Repository, 1991. https://repository.hkbu.edu.hk/etd_ra/7.

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Burrows, Mark Robert. "Landfill hydrogeology and the hydraulic properties of in situ landfilled material." Thesis, Royal Holloway, University of London, 1998. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.286066.

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Zhang, Chi. "Struvite Precipitation of Ammonia from Landfill Leachate." Thesis, Université d'Ottawa / University of Ottawa, 2016. http://hdl.handle.net/10393/34492.

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The application of struvite (magnesium ammonium phosphate,!MgNH&PO& ∙ 6H+O) precipitation and its recycling use for the purpose of ammonia removal from both synthetic solutions and landfill leachate were investigated in this study. The results demonstrated that chemical precipitation by struvite formation is efficient for ammonia removal from aqueous solutions. In addition, by recycling the thermal residue of struvite, continuously removing ammonia can technically be achieved. In the struvite precipitation, ammonia removal significantly depended on the pH and chemical molar ratios of NH& ,:!Mg+,:!PO& ./. For synthetic solution (TAN=1,000 mg/L), remarkable TAN removal efficiency of over 98% has been reported when the molar ratio of NH& ,:!Mg+,:!PO& ./ equals 1.0:1.2:1.2, 1.0:1.3:1.3, 1.0:1.3:1.4 and 1.0:1.5:1.5 at optimum pH 9. The optimum combinations of reagents applied in landfill leachate (TAN=1,878 mg/L) were!NH& ,:!Mg+,:!PO& ./ =1.0:1.3:1.3, 1.0:1.4:1.3, 1.0:1.5:1.4 and 1.0:1.5:1.5 at optimum pH 9.5, all of which displayed excellent TAN removal efficiencies of over 99%. Response surface method (RSM) helped to analyze the data and optimize the results. The struvite pyrolysate provided best performance of removing ammonia in both simulated wastewater and landfill leachate at a dosage of 60 g/L, when struvite was previously heated at 105 􀀁 by oven for 2.5 h. In the recycling phase, the struvite pyrolysate resulting from NaOH-mediated pyrolysis was more effective at continuously treating ammonia synthetic solution than was direct heating, with an initial mode of 87.4% at the beginning to 75.1% in the fifth round and direct heating of struvite from 80.9% in the first cycle and 60.6% in the final cycle. The struvite pyrolysate formed by NaOH-mediated pyrolysis performed with greater ability to continuously eliminate ammonia from landfill leachate (97.2% removal at the beginning and 72.3% in the fifth round), than did directly heated struvite (98.4% in the first cycle and 81.3% in the final cycle). Additionally, microwave irradiation could also dissociate struvite, which subsequently demonstrated moderate TAN removal in recycling phases.

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Brachman, Richard W. I. "Mechanical performance of landfill leachate collection pipes." Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1999. http://www.collectionscanada.ca/obj/s4/f2/dsk1/tape8/PQDD_0006/NQ42503.pdf.

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Nie, Jing. "Landfill Leachate Treatment by Fenton's Reagent Oxidation." Thesis, University of Louisiana at Lafayette, 2015. http://pqdtopen.proquest.com/#viewpdf?dispub=1585908.

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<p> Fenton's Reagent Oxidation can significantly enhance the COD removal efficiency of landfill leachate. The results presented in this thesis show that the maximum amount of COD that could be removed by Fenton's Reagent Oxidation was about 80% of the initial value. Such a maximum removal was achieved using reagent dosage of 300 mg/L of H<sub>2</sub>O<sub>2</sub>, 55.84 mg/L of Fe<sup> 2+</sup>, and a pH of 3 at 25°C. </p><p> A mechanistic model was developed based on the kinetic reactions. A coefficient α, representing the proportional constant between organic matter and COD was firstly introduced to this model. This model fit the data well. The modeling coefficients of α, [·OH] and <i>k</i><sub>7</sub> are 0.013mol <i>mg</i><sup>-1</sup>, 1.65×10<sup>-9</sup> <i> M</i> and 1.55×10<sup>-9</sup> <i>M</i><sup>-1 </sup><i>s</i><sup>-1</sup>, respectively. Hydroxyl radical concentration was calculated and the results confirm the pseudo steady state assumption. Response surface design and analysis results predicted that COD remaining can achieve the lowest value of 48 mg/L with the treatment conditions of a reaction time of 3.8 hours, a pH of 2.3, and a mass ratio of H<sub>2 </sub>O<sub>2</sub> to Fe<sup>2+</sup> of 38 at 60°C.</p>

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Ochieng', Otieno Frederick A. "Impact of recirculation on landfill leachate quality." Thesis, University of Newcastle Upon Tyne, 1989. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.235556.

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Freewood, Robert John. "Landfill leachate attenuation characteristics of colliery spoil." Thesis, University of Sheffield, 2001. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.390711.

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Books on the topic "Landfill leachate"

1

Pazoki, Maryam, and Reza Ghasemzadeh. Municipal Landfill Leachate Management. Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-50212-6.

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Souabi, Salah, and Abdelkader Anouzla, eds. Landfill Leachate Treatment Techniques. Springer Nature Switzerland, 2024. http://dx.doi.org/10.1007/978-3-031-63157-3.

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Anouzla, Abdelkader, and Salah Souabi, eds. A Review of Landfill Leachate. Springer Nature Switzerland, 2024. http://dx.doi.org/10.1007/978-3-031-55513-8.

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O'Neill, Hugh J. Leachate management at Croreagh landfill site. The Author), 1998.

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Davies, S. P. The aerobic treatment of landfill leachate. UMIST, 1993.

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Maloney, Stephen W. Sanitary landfill leachate recycle and environmental problems at selected Army landfills: Lessons learned. US Army Corps of Engineers, Construction Engineering Research Laboratory, 1986.

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Walter, Chiang, ed. Sanitary landfill leachate: Generation, control, and treatment. Technomic Pub. Co., 1994.

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Walter, Chiang, ed. Sanitary landfill leachate: Generation, control, and treatment. Routledge, 2017.

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George, Fleming, and University of Strathclyde. Department of Civil Engineering., eds. Proceedings of leachate and landfill gas control in landfills: Environmental legislation and practice. University of Strathclyde, Dept. of Civil Engineering, 1992.

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Geological Survey (U.S.), ed. Schlumberger soundings at the Norman Landfill, Norman, Oklahoma. U.S. Dept. of the Interior, Geological Survey, 1996.

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Book chapters on the topic "Landfill leachate"

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Akgün, Haluk, and Jaak J. K. Daemen. "Landfill landfill/landfilling Leachate Control landfill/landfilling leachate control." In Encyclopedia of Sustainability Science and Technology. Springer New York, 2012. http://dx.doi.org/10.1007/978-1-4419-0851-3_112.

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Pazoki, Maryam, and Reza Ghasemzadeh. "Leachate Quality." In Municipal Landfill Leachate Management. Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-50212-6_3.

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Pazoki, Maryam, and Reza Ghasemzadeh. "Leachate Quantity." In Municipal Landfill Leachate Management. Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-50212-6_4.

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Pazoki, Maryam, and Reza Ghasemzadeh. "Leachate Management." In Municipal Landfill Leachate Management. Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-50212-6_5.

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Cherni, Yasmin, Sarra Hechmi, Samira Melki, Mohamed Ali Wahab, and Ismail Trabelsi. "Landfill Leachate Characteristics." In A Review of Landfill Leachate. Springer Nature Switzerland, 2024. http://dx.doi.org/10.1007/978-3-031-55513-8_3.

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Waara, Sylvia. "Landfill Leachate Ecotoxicity." In Encyclopedia of Aquatic Ecotoxicology. Springer Netherlands, 2013. http://dx.doi.org/10.1007/978-94-007-5704-2_61.

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Aziz, Hamidi Abdul, Mohamed Shahrir Mohamed Zahari, Zaber Ahmed, et al. "Landfill Leachate Treatment." In Solid Waste Engineering and Management. Springer International Publishing, 2022. http://dx.doi.org/10.1007/978-3-030-96989-9_8.

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Pazoki, Maryam, and Reza Ghasemzadeh. "Waste Management." In Municipal Landfill Leachate Management. Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-50212-6_1.

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Pazoki, Maryam, and Reza Ghasemzadeh. "Landfilling." In Municipal Landfill Leachate Management. Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-50212-6_2.

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Pazoki, Maryam, and Reza Ghasemzadeh. "Natural Treatment Systems." In Municipal Landfill Leachate Management. Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-50212-6_6.

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Conference papers on the topic "Landfill leachate"

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Long, Tao. "Research of pretreatment for reverse osmosis in landfill leachate treatment process." In Fifth International Conference on Green Energy, Environment, and Sustainable Development, edited by Mohammadreza Aghaei, Hongyu Ren, and Xiaoshuan Zhang. SPIE, 2024. http://dx.doi.org/10.1117/12.3044421.

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Upadhyay, Kshitij, and Samir Bajpai. "Transport of Microplastics from Municipal Solid Waste Landfills to Aquatic system: An Overview." In International Web Conference in Civil Engineering for a Sustainable Planet. AIJR Publisher, 2021. http://dx.doi.org/10.21467/proceedings.112.27.

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Microplastics possess a significant threat to water resources as well as aquatic life and present a challenge in overall water resource management. Among a wide variety of entry routes available for microplastics from land to water bodies, municipal solid waste (MSW) landfills are suspected to be one of the important land-based sources (entry point) of microplastics affecting water quality. Few studies reported the presence of microplastic in the leachate obtained from municipal solid waste landfills corroborating that MSW landfills not only act as a sink of microplastic pollution but also act as a source. Microplastics from these leachates move to the soil system thereby affecting its quality and further migrate to aquatic systems. This movement of microplastic from leachate to aquatic system not only deteriorate the water quality but also highlights the importance of land-based sources of microplastic. In this review, we focused on the role of landfills as a pathway for microplastics to water bodies. The main aims of this review the abundance and characteristics of microplastics in landfills and discuss the role of landfill age. Polyethylene in fragmented and fibrous form remains the predominant type and shape of microplastic in leachates. The shape, size, and abundance of microplastics in leachates vary with landfill age. Landfills also provide a favorable environment for microplastic degradation thereby turning macroplastics into tiny plastic pieces. The major type of degradation is oxidative degradation. Our review confirms that MSW landfills are indeed a source of microplastic and contribute to microplastic pollution in soil and aquatic systems.

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Yan-jiao Gao. "Landfill leachate treatment by electrocoagulation." In 2011 Second International Conference on Mechanic Automation and Control Engineering (MACE). IEEE, 2011. http://dx.doi.org/10.1109/mace.2011.5987671.

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Kuusik, Aare, Karin Pachel, Argo Kuusik, and Enn Loigu. "Landfill runoff water and landfill leachate discharge and treatment." In The 9th International Conference "Environmental Engineering 2014". Vilnius Gediminas Technical University Press “Technika” 2014, 2014. http://dx.doi.org/10.3846/enviro.2014.083.

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Mussa, Zainab Haider, Mohamed Rozali Othman, and Md Pauzi Abdullah. "Electrocoagulation and decolorization of landfill leachate." In THE 2013 UKM FST POSTGRADUATE COLLOQUIUM: Proceedings of the Universiti Kebangsaan Malaysia, Faculty of Science and Technology 2013 Postgraduate Colloquium. AIP Publishing LLC, 2013. http://dx.doi.org/10.1063/1.4858758.

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Matthews, R. J., M. K. Winson, and J. Scullion. "Aerobic biological treatment of landfill leachate." In WASTE MANAGEMENT 2006. WIT Press, 2006. http://dx.doi.org/10.2495/wm060461.

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Bai, W. K., F. Liu, and H. You. "Enhanced Coagulation for Landfill Leachate Pretreatment." In International Workshop on Environmental Management, Science and Engineering. SCITEPRESS - Science and Technology Publications, 2018. http://dx.doi.org/10.5220/0007561704310436.

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Zhang, Rongxin, Jinxiang Fu, Xingguan Ma, Yunlan Tan, Jun Li, and Kun You. "Conventional Treatment of Nitrogen in Landfill Leachate." In 2010 4th International Conference on Bioinformatics and Biomedical Engineering (iCBBE). IEEE, 2010. http://dx.doi.org/10.1109/icbbe.2010.5517058.

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Zhang, Shengli, Lei Jiang, Dan Liu, and Bin Li. "Organic Contamination and Biodegradability of Landfill Leachate." In 2010 4th International Conference on Bioinformatics and Biomedical Engineering (iCBBE). IEEE, 2010. http://dx.doi.org/10.1109/icbbe.2010.5517898.

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Tian, Yu, Wenwei Zhang, Jianhua Tang, and Wen Li. "The recharge method of landfill leachate treatment." In 2015 3rd International Conference on Advances in Energy and Environmental Science. Atlantis Press, 2015. http://dx.doi.org/10.2991/icaees-15.2015.137.

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Reports on the topic "Landfill leachate"

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Bogner, J., and K. Spokas. Effect of leachate recirculation on landfill gas production and leachate quality: A controlled laboratory study. Office of Scientific and Technical Information (OSTI), 1995. http://dx.doi.org/10.2172/67771.

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McQueen, Andrew, O’Niell Tedrow, Mark Ballentine, and Alan Kennedy. Demonstration of photocatalytic degradation of Per- and Polyfluoroalkyl Substances (PFAS) in landfill leachate using 3D printed TiO₂. Engineer Research and Development Center (U.S.), 2025. https://doi.org/10.21079/11681/49606.

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Per- and polyfluoroalkyl substances (PFAS) are recalcitrant substances present globally in many landfill wastewater leachates and have potential ecological and human health risks. Conventional treatment technologies have shown limited efficacy for many PFAS due to the stable C–F bonds. Therefore, there is growing interest in applying advanced oxidation processes to decrease the aqueous concentrations in contaminated wastewater and mitigate risks. The goal of this study was to evaluate the photocatalytic performance of treating PFAS in landfill leachate using a novel photocatalyst composite. Treatment structures were fabricated using polylactic acid and compounded with TiO₂, and 3D printed into tiles. A pilot-scale treatment system was designed to promote photocatalysis using 3D composite structures and UV irradiance intensity of 1.0 mW cm⁻² following 24- and 36-h hydraulic retention times. Photocatalytic degradation was achieved for seven of the 11 PFAS evaluated in this study. Greater than 80% removal of PFOS, PFNA, PFDA, and PFOSAm was observed after 24 h of photocatalysis. These results indicate photocatalysis using TiO2 polymer composites can achieve beneficial levels of PFAS degradation. This study provides a proof-of principle approach to inform the application of additive manufacturing of photocatalytic composites for use in the treatment of PFAS-contaminated wastewater.

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Peverly, J., W. E. Sanford, and T. S. Steenhuis. Constructed wetlands for municipal solid waste landfill leachate treatment. Final report. Office of Scientific and Technical Information (OSTI), 1993. http://dx.doi.org/10.2172/10133187.

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Schock, Kevin. Predicting Seepage of Leachate from the St. Johns Landfill to Ground and Surface Water Systems. Portland State University Library, 2000. http://dx.doi.org/10.15760/etd.6532.

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Reis, J. R. Town of Colonie sanitary landfill leachate management system. Final report for 1992 and 1993 spraying season. Office of Scientific and Technical Information (OSTI), 1996. http://dx.doi.org/10.2172/374122.

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Hydrogeology and leachate plume delineation at a closed municipal landfill, Norman, Oklahoma. US Geological Survey, 2002. http://dx.doi.org/10.3133/wri014168.

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Leachate treatment system using constructed wetlands, Town of Fenton sanitary landfill, Broome County, New York. Final report. Office of Scientific and Technical Information (OSTI), 1993. http://dx.doi.org/10.2172/10133188.

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Ground-water hydrology and the effects of vertical leakage and leachate migration on ground-water quality near the Shelby County landfill, Memphis, Tennessee. US Geological Survey, 1991. http://dx.doi.org/10.3133/wri904075.

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Geohydrology of the unsaturated zone and simulated time of arrival of landfill leachate at the water table, municipal solid waste landfill facility, US Army Air Defense Artillery Center and Fort Bliss, El Paso County, Texas. US Geological Survey, 1999. http://dx.doi.org/10.3133/wri974036.

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