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Waste Treatment - Science topic

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Les géopolymères offrent plusieurs propriétés intéressantes qui peuvent être exploitées dans diverses applications innovantes :
1. Construction durable :
- Bétons à faible empreinte carbone
- Matériaux de construction résistants au feu et aux produits chimiques
2. Traitement des déchets :
- Encapsulation de déchets toxiques ou radioactifs
- Valorisation de cendres volantes et autres sous-produits industriels
3. Aérospatiale :
- Matériaux composites légers et résistants pour l'aviation
- Revêtements protecteurs pour engins spatiaux
4. Énergie :
- Composants pour piles à combustible
- Matériaux de stockage d'énergie thermique
5. Restauration du patrimoine :
- Réparation et consolidation de structures anciennes
6. Industrie :
- Revêtements anti-corrosion pour équipements industriels
- Filtres et membranes pour le traitement de l'eau
7. Impression 3D :
- Nouveaux matériaux pour l'impression 3D à grande échelle
8. Médecine :
- Biomatériaux pour implants et régénération osseuse
Ces applications tirent parti des propriétés uniques des géopolymères telles que leur résistance mécanique, leur durabilité chimique, leur stabilité thermique et leur faible impact environnemental.
Quelles autres applications peut on imaginer
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Les géopolymères offrent plusieurs propriétés intéressantes qui peuvent être exploitées dans diverses applications innovantes. Voici quelques-unes des applications potentielles :
1. **Construction durable** :
- Bétons à faible empreinte carbone
- Matériaux de construction résistants au feu et aux produits chimiques
2. **Traitement des déchets** :
- Encapsulation de déchets toxiques ou radioactifs
- Valorisation de cendres volantes et autres sous-produits industriels
3. **Aérospatiale** :
- Matériaux composites légers et résistants pour l'aviation
- Revêtements protecteurs pour engins spatiaux
4. **Énergie** :
- Composants pour piles à combustible
- Matériaux de stockage d'énergie thermique
5. **Restauration du patrimoine** :
- Réparation et consolidation de structures anciennes
6. **Industrie** :
- Revêtements anti-corrosion pour équipements industriels
- Filtres et membranes pour le traitement de l'eau
7. **Impression 3D** :
- Nouveaux matériaux pour l'impression 3D à grande échelle
8. **Médecine** :
- Biomatériaux pour implants et régénération osseuse
Ces applications tirent parti des propriétés uniques des géopolymères telles que leur résistance mécanique, leur durabilité chimique, leur stabilité thermique et leur faible impact environnemental.
D'autres applications potentielles incluent :
9. **Écologie** :
- Matériaux pour la restauration et la protection des écosystèmes
10. **Biotechnologie** :
- Matériaux pour la culture cellulaire et la bioproduction
11. **Automobile** :
- Matériaux pour les carrosseries et les composants automobiles
12. **Électronique** :
- Matériaux pour les circuits imprimés et les composants électroniques
13. **Nanotechnologie** :
- Matériaux pour les nanofiltres et les nanocomposants
14. **Géothermie** :
- Matériaux pour les réservoirs de stockage de chaleur géothermique
15. **Biomatériaux avancés** :
- Matériaux pour les implants biomédicaux et les dispositifs médicaux
Ces applications innovantes continuent de se développer en tirant parti des propriétés uniques des géopolymères, offrant des solutions durables et écologiques pour divers secteurs industriels et de la recherche.
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In 'life cycle' under product stages we can give 'waste disposal' process,how does this impact the result?
And under product stage there is also option to make 'waste treatment' stage.So how to analyze this or use it in the impact assessment?
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Waste/disposal scenario" in SimaPro models the final disposal of waste, while "waste treatment" represents pre-disposal treatment processes. Both are essential for assessing the environmental impacts of waste management in a product's life cycle.
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I am working on medical waste treatment problems&solutions, and I need preferably a technical overview of the various equipment used in healthcare waste management (combustion, autoclaving, shredding).
Can anyone suggest a textbook or article where I can find that?
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The pandemic added extra medical waste to the global healthcare systems, with 1.56 billion face masks ending up in oceans in 2020 alone. Here are ideas to fix the system...
Adopting a circular economy – keeping materials and products in circulation for as long as possible, can help reduce waste and lower environmental impacts including climate change. Supply chains play a big role in ensuring that product design, procurement of raw materials, and the manufacturing, distribution, and reverse logistics processes become less resource intensive, and have the ability to re-capture waste to manufacture new materials and products. From procurement and inventory planning to storage and waste management, healthcare leaders have recognized that their supply chain operations were substantially affected by COVID-19. A recent McKinsey survey3 of US health systems executives highlighted that 75% of survey respondents say that moving forward, supply chain needs to assume a more strategic role within the healthcare system...
Here are four areas healthcare leaders should take into consideration when it comes to managing waste in a sustainable way:
  • Taking a data-first approach
  • Collaborating with suppliers, ensuring sustainable procurement and manufacturing innovation
  • Maintaining real-time inventory visibility
  • Proper classification of materials, segregation and reverse logistics...
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Sugarcane filter cake is one of the sugar industry waste which produce in a large quantities and has a potency to process as a biomass. What is the future idea for the utilization of sugarcane filter cake in industry?
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The composition of press mud generated is influenced by locality, cane variety, milling process and the clarification process chosen for sugar purification. Main components of press mud are moisture (50–65%), fibre (15–30%), crude wax (5–14%), sugar (5–15%), crude protein (5–15%) and nitrogen (2–2.5%). It is a potential source of hydrocarbons and valuable chemicals through thermochemical conversion processes.
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Material recycling is of high relevance for LCA of Waste management systems. Lately, the material "upcycling" term has been voiced by a variety of stakeholders. How do you deal with it while modeling your e.g. MSW management system?
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One manifestation of material 'upcycling' can be 'chemical recycling'. Recent studies have been published by companies like BASF, Plastic Energy, and independent think tanks like The Consumer Goods Forum that will be useful to read for this.
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The traditional construction of a composite indicator is generally based on Factor analysis or Principle Component Analysis. These two methods require that individual indicators are supposed to be correlated to each other to some extent (e.g., factors in the correlation matrix are larger than 0.5). This precondition could guarantee that these individual indicators describe a similar phenomenon.
However, in my case, there are 5 individual indicators representing waste treatment behavior from different perspectives (e.g., sewage treatment methods, domestic waste treatment, agricultural production waste treatment....). These indicators are less correlated to each other, which cannot satisfy the requirement for the application of FA or PCA(cannot pass KMO test). Based on this, what should I do if I want to use one composite indicator to capture treatment behavior?
By the way, these 5 individual indicators are valued by 1,2,3, and 4. The larger the number, the more environmentally friendly the treatment method is. Do you think it is feasible if I calculate the sum of these 5 indicators directly?
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Dear Xiong
The fact that you don't use weights does not mean that a method like SIMUS does not consider tehm. Quite rthe opposite, SIMUS is an iterative method, and thus, the COMPLETE SET of weights are computed internally at each iteration, based on data, maybe hundreds of times. However, these weights do not correspond to experts estimates.
In SIMUS, once you get the final result completely based on certain data, either quantitative or/and qualitative, it is the DM task to analyze the result and make as many changes as as she/he wants, based not onloy on experience and know-how, but also from consultationsd with stakeholders
In this way, you estimate how the results are in agreement with what each stakeholder wants, and of course, it can be corrected many times, until reaching a compromise solution that satisfies all stakeholders.
Refernce to you question, the answer is yes, you can apply subjective weights from stakeholders. Just multiply the subjective weight, by the values of each criterion, before building the initial decision matrix. You can proceed as group decision making.
But you don't need to do as you say in the case of wastes, because thus, you are considering the value of only one criterion and leave the other criteria with a same weight. As you can see, it does not have any mathematical support. First, because thre selection of the criterion with the highest weight is arbitrary, and second, because you can't assume that the other remain equal.
In reality, what you are proposing is what SIMUS does. It takes sewage disposal as objective subject to the other criteria. Then, replace it in the matrix and uses waste separation, as a second objective, and so on, but SIMUS does not use any weight.
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There is a remarkable rise in the size of affluent middle class in developing countries like India. This means consumption and the resulting plastic waste generation are also increasing at a high pace. Unfortunately, more often than not, I see that the municipality infrastructure for waste collection and disposal has not kept up with the pace. I am wondering if there are already applied practical solutions for waste treatment at homes which do not have to rely on government infrastructure, for eg: small incinerators for homes. I am curious to hear other perspectives on this.
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Whereas, Composting is the simplest and easiest way to treat domestic waste.
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I am trying to calculate carbon footprint of a 1km Cable, but cant find emission factor for lubricant i kinda need its GWP emission factor as raw material and GWP emission factor as its average waste treatment !
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Dear Hamza Karmoum,
The study sounds interesting. You might try to go to the enterprise and do field research to get the emission factors. Some LCA emission factors can only be obtained through field research.
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I read an article regarding electrocoagulation of restaurant wastewater, and doesn't say anything about the condition of the wastewater before undergoing the treatment, so is it safe to say that temperature has no effect on the process? And is it also safe to assume that the process is at standard conditions?
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The effect of temperature may be explained by considering conductivity. Water conductivity increased at high temperature, leading to an increase in removal efficiency up to 25 and 30°C. On the other hand, further increase in temperature more than 30°C destabilized the dye adsorption on hydroxide and, thus, decreased removal efficiency.
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I'm not sure the steps to treat wastewater containing mixture of alcohol solvent, oils and glycerol. do we neet to separate before further treatment.
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In my opinion, at first, we need to know the concentration of target pollutants to be able to choose the most suitable treatment system.
For example, when the concentration of pollutants is very high it is necessary to think about physical treatment, if the concentration is lower, we can think about biological treatment. And also if we want to find the most suitable treatment technology(ies), we need to know what is the treatment limit (what should be the final concentration of pollutants in treated wastewater).
Regards
Vit
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Nitrogenous compounds are very common in wastes, both in liquid and solid wastes from the industries. These also have an adverse effect on the environment. In the case of nitrogenous compounds contaminated wastes treatment, there are several methods used worldwide. One of them is the Land Application Technique.
In this process, wastewater stabilization ponds and lagooning techniques are used. My question is, How much effective the land application technique is, compared to physio-chemical and biological methods?
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For Manure Application
Land application to meet crop N, P, and other nutrient requirements is by far the most widespread and longstanding use of animal manures. However, other uses do exist and are becoming more common, especially in areas where animal production has become so intensive that the amount of nutrients in the manure produced exceeds the nutritional requirements of crops grown on the local land base. Sometimes manure is fed back to animals as a cheap nutrient source (e.g., feeding chicken litter to beef cattle). However human and animal health concerns have been raised about this practice, in the wake of the ‘mad cow disease’ outbreak in Europe (caused by feeding contaminated animal products back to cattle), and this is not viewed today as a major alternative to land application of manures. Mushroom production in certain areas can use large amounts of manure, especially from horses and poultry. In China, manures are used extensively in fish production. Several other options exist for manure use, and although these uses are only carried out on a relatively small scale today, they represent a growth area, as increasing intensification of agriculture produces excess amounts of manure in localized areas of more countries. Examples of other manure uses are composting to produce high-value soil amendments, methane generation via anaerobic digestion, burning to generate energy, and pelletizing manures to make organic fertilizers.
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Why would one choose this process say, over an MBR process. In a vacuum, how would you justify selecting a UCT process over another? Thanks!
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Biological Nutrient Removal Activated Sludge (BNRAS) systems remove carbon, nitrogen and phosphorus by biological means with low costs and less waste sludge production. One of the most commonly applied BNRAS methods for urban wastewater treatment relies on the University of Cape Town (UCT) concept.
The beneficial characteristics of the proposed optimum plant configuration are plentiful. The initial anaerobic tank helps select phosphate accumulating organisms, according to the enhanced biological phosphorus removal technique, as well as floc-formers over filamentous bacteria. The three denitrification cascade yields to high removal efficiency and also offers operational safety. Influent flow rate is distributed to anaerobic or anoxic tanks (step feeding process) to provide organic substrate for phosphate release and denitrification, as well as to transform these tanks into selectors of floc-formers over filaments.The theoretically expected design advantages also.
Denitrifying phosphorus removal dual sludge system had low energy needs and oxygen requirement. Solve the competition on matrix and nutrient between species, and reduced the number of sludge return system, compared with single sludge system.
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I have seen the enormous slurry test site at Deltares and heard people about the test which will be run with it. Waste water sytems in the Netherlands become more slurry like through uncoupling rain/stormwater systems. I am curious if there are new recommendations for minimal and maximal speed for waste water fluid streams, if the become more slutty like. Are there more aspects, on which we as developers of waste water pumps and systems, should be aware of?
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Dear Frits,
last oktober this thesis :(https://www.saniwijzer.nl/media/stowa_saniwijzer_v2/org/1/documents/thesis_slurry_hydraulics_radhakrishnan.pdf) was published based on the results of this project.
If you need any information pls contact me.
kind regards
Francois Clemens
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Sorry, not research related but people on here are helpful.
My current flow sheet is linked above. I am open to any critique or advice as it is all helpful. I am currently working on the distillation columns at which point I will proceed to economics and selection of equipment. But my question actually regards the ammonia in my system. Excess ammonia is fed in two different cases to support two different distributions of MEA/DEA/TEA in the product stream where the equipment must remain the same (AKA same plant) but the operating conditions can be altered to support multiple distributions. I recycled the ammonia due to excess and the presented cost of waste treatment but I began considering a scrubber instead. I modeled a radfrac column as a scrubber with water and it worked but required too much water.
QUESTION:
I discovered their method was to scrub it the same way essentially but with a 97% sulfuric acid solution which neutralized with ammonia to form ammonium sulfate (marketable). I was appealed to the idea of this since the process used so much excess ammonia and I was uncomfortable with the idea of re-condensing after the flash to feed-stock conditions. I am unsure of how to model the mass transfer limited rate of reaction considering it is a gas reacting with a liquid and the reaction is essentially instantaneous.
My other idea is to keep the recycle stream and instead react the condensed purge stream with sulfuric acid and not have to worry about modeling the mass transfer. This could also be appealing if I am making too much ammonium sulfate by scrubbing all of the ammonia and not recycling it, and my professor dings me for not being able to sell it. I am still unsure of how to find the kinetic parameters for the reaction though.
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Hi, what are the kinetic parameters for the MEA DEA TEA reactions? Thank you
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As I am trying to capture CO2 by bio-filtration process so I ran into a few problems. I was thinking perhaps you are able to help me with them.
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Designing of tanks for dye waste treatment plant.Dye waste treatment plant consists of two tanks, equalising and Neutralizing tanks.
Dye waste from different industries consists of different chemicals which will affect the concrete directly.
It is possible to construct treatment plant without any equalising tank?
Waste that from industry can directly fed to Neutralizing tank and then to other treatment process?
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Bala Murali: It is a big problem to treat wastewater without knowledge what should be removed. I had an experience from Gujarat with a wastewater treatment plant for treatment of wastewater from a cluster of various plants (textile, dying, production of chemicals and pharmaceuticals ....). The solution for this case was to make inventory of all wastewaters comming to the wastewater treatment plant and in some cases install a pretreatment system at the place before wastewater mixing. This solution improved efficiency of wastewater treatment and decreased operational costs by 17 %. The pretreatment systems reduced the most problematic pollutants for much lower costs in comparison to elimimnation of these pollutants from huge amount of mixed wastewater.
Best regards
Vit
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I am confused between plasma arc and plasma jet. Are they same thing?
I am interested in Plasma Waste Treatment Technology using plasma torches.
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the difference for plasma waste is
- plasma arc is a current conductor, and can burn niether between cathode or anode inside plasmatorch(non transfered type plasma torch), or from cathode inside plasma torch on treated material(transfered type plasmatorch). In that case material should be conductive. The gas inside and around an arc is intensivly heated by Ohm's heat release.
-plasma jet is just a jet of heated partly dissosiated gas, in plasmatorches it is produced (the gas is heated) with arc inside plasmatorch.
the desicion what type of plasmatorch should be used depends on a treated material and other industrial conditions
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How I can study the growth curve of the algal biomass in the water sample collected from natural water bodies or from oxidation pond of waste treatment plant while the algal species are unknown?
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Hello,
First you need to ensure that no additional inputs of new populations of algae are introduced after the initial measurement. Because in a dynamic environment that is always the case as new additions can happen either as unidirectional current carried cells or upwelled cells. Hence quite difficult to monitor biomass growth unless you are monitoring it on hourly basis and then the mean value of a certain period can be compared with the next day, although fraught with errors.
In a stagnant body however, it is comparatively easy but still you have to be careful. Different part of the day yields different values of chlorophyll contents as it is dependent on the supply of element like carbon, magnesium and manganese and iron etc. And the biggest factors are the light intensity and ambient temperature. If your sampling pond/body is stagnant them you need to ascertain the time of sampling and measure the temperature and light flux at the surface and/or at the depth of your sampling and keep on monitoring the same parameters every day for a certain period at the same time and try to collect sample within the range of the parameters of the first sampling period to yield a comparable data. The comparison can be made as mean number of cells (when dealing with populations) per unit volume, mean surface area/biovolume of the cells collectively or for a specific specific or the amount of mean chlorophyll a concentration per unit volume.
I hope this helps you.
Dr. Abhishek Mukherjee
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Dear all,
I read from the new version of TIMES document (Part II Refernece manual) that
An inter-period storage process is able to store energy or material over periods. For example, a coal stockpile or a waste disposal site can be modeled as an inter-period storage.
and
Modeling of methane emissions from landfilling in a dynamic way by using first-order decay functions for the gradual waste decomposition (optionally with different rates of decay for different waste qualities);
Actually, I'm trying to introduce the landfilling process into my VEDA-TIMES model, but I found that there was no clear example that can be refered to. So could anyone share their experiences in solving this problem or is there any example in such field? Thank you all in advance~
Best wishes!
Xin WANG
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I have read articles about using flotation to separate a variety of materials, and of course, the majority application of this tech is used in mining. However, I can only find quite a limited number of papers talking about using flotation to harvest cells or microbes, such as E.coli, and most of those papers are quite old (around 1960 to 1970s). I don't know why people nowadays don't talk about its application in microbe separation like other methods, such as ultrafiltration and centrifugation. Is there any critical fact that I missed kicking this method out from the industry of microbe separation, or could it because this method is so classic that people don't waste a word to talk about it? 
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From practical point of view: the flotation has rather low efficiency (a lot of produced biomass is lost).
We employ denitrification flotation for waste activated sludge thickening in full scalůe with succes. See the proces BIOFLOT.
Best regards
Vit
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I need to have the investment costs, operation and maintenance costs of a dark fermantative hydrogen production plant from waterwaste and solid waste
thank you
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about methods of wastewater treatment
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You can work on "DEWATS" system for human sludge management.
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I am designing a process based in a solid catalyst (a 40 um -sized powder) to perform a liquid-phase reaction. At the end, a slurry is obtained, from which catalyst must be separated to be reused.
Does anyone know which is the preferred way to acomplish this at the industrial level? Is the slurry taken out of the reactor and filtrated in a dedicated equipment? or is there an established procedure to do it inside the reactor, this is, with no need for additional equipment (i.e. filter)? I have not found any precise literature examples so far.
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What are the main differences between an ebullated reactor and a slurry reactor?
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Hello, 
I am currently working on a research about the different types of solid waste produced from meat working/finishing industries. I am looking to calculate the cost of disposing the wastewater sludge ( Classification number 190205 ,according to AVV Standard). Is there any reasearch done on the costs,can anyone help me in finding out the cost required to dispose per tonne of wastewater sludge to an external disposal company?
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Perhaps an alternative view is to consider either how to process this waste into something less hazardous or into a revenue stream.  The material is impregnated with the short fibers reamining from toilet paper that bind with the water to make this material expensive to dispose. The cost of disposal is tied to the fact that this is over 80% water.  This colloid needs to be broken if this cost is to be reasonable.  The sewer cake can be broken down and the water recycled back for reprocessing and remaining grit/sand can be used as land fill cover.  Integrated BioChem has shown that sewer cake can broken down.  .  Attached is a photograph showing the breakdown of sewer cake using our MEF technology.
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We need to make the determination of Lower Calorific Power to samples of the organic fraction of municipal solid waste, with the objective of its valorization.
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Many thanks.
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I am involved with the removal of oil and water from solids (drilled formation cuttings) and the recovery of the oil phase for reuse. Thermal plants are capable of this, but too often the separated oil carries over detrimental quantities of ultra-fine solids. I am seeking technologies that at least provide a clean (solids-free) oil. Or alternatively wanting to identify a practical method of removing the ultra-fine solids from the processed solids. 
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Hello Reagan
Various separations of 3-phase streams, (oil, liquor, solids) have been performed in 'solid-bowl' centrifuge. 'Tri-canter' designs that have been applied in hydro-metallurgy applications generally deliver 'cleaner' products compared to 'vertical-splindle' machines; e.g Flottweg, GEA,.
regards
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Industrial and engineering brick manufacturing by mixing certain ratios of wastewater treatment plant sludge + clay.
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I know, I am looking for a new procedure or facility regardless to determine the plasticity index, plasticity and liquid limits of soil samples.
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Is this viable? Has anyone done this?
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Carbon nanotubes.
I think the problems with plastic waste are
dyes like titanium dioxide, and chlorine (PVC).
Regards,
Joachim
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just to know more about hydrothermal treatment for produced water, drilling water, completion waste and waste water
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Good papers thank you for it Prof. Bachir
Regards
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I am planning to buy an ozone generator for lab use. If I could get the website and pricing that would be very helpful.
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The very basic ones you can find on sites like aliexpress, starting from usd 20.
We have one installed on a simple timer running for 15 minutes at night.
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Hi 
Your work is very interesting, I'm just curious as to whether the effluent stream from pulp and paper mills which contain lignocellulosic biomass is being investigated as an option for an AD biorefinery? 
Regards
Charlotte Wessels
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Hello Charlotte,
Basically it is a standard (continuous or SBR) activated sludge system (retrofit) upgraded with a contact step (selector) at the inlet/feed and a regeneration step of the settled/recycled activated sludge after clarification (RAS in continuous system). This setup boosts the adsorption capacity of the biosludge and enhances the hydrolysis of the recalcitrant compounds previously adsorbed on (and enmeshed in) the biosludge flocs. In this way we achieve ultralow residuals (COD, turbidity, SDI, ...) even compared to well designed MBR's. We develop and apply our AS+(tm) process at full scale over the last 30 years. If interested I can send you more information via email.
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I am intrested in knowing COD/BOD reduction in primary treatment of paper mill effluent. The mill effluent contains very high TSS, mainly contributed from deinking process.  If anyone has experience or case study.
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I have gone through many research papers regarding composting and have observed that the reduction in heavy metal concentration is seen with an effective percentage but I have a doubt because a coworker of mine suggested that there is no reduction an the heavy metal concentration and they only transform from one form to other. The total quantity remains the same. These are two contradictory statements. I would appreciate if some light will be thrown on this issue.
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As heavy metals are elements they cannot be destroyed or removed from composted waste through alteration or degradation. The reply above is correct that, given suitable pH etc, metals will often sorb onto and be immobilised by organic matter. As I understand, the only way that the overall concentration might alter is if uncontaminated material is added to the compost to dilute the metal concentration or if specific techniques are used to remove contaminated particles (these are often the smaller size fraction of MSW). For the latter reason, metal conc. of composts produced from MSW have declined over time as processing technology has improved and sources of contamination have been physically removed, usually prior to composting. Hope this helps, there is plenty in the literature on this topic published by Bardos (2004) and others.
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I'm using 2o-litre plastic containers as airtight reactors and 5 litres of cowdung slurry as inoculum. 
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I guess the expected biogas production mainly depends on the contents of both dry matter (DM) and lignin (% of DM) of the kitchen waste (KW):
1) Assuming a DM of let's say 25%, 1 kg of KW consists of 0.25 kg DM.
2) Assuming a relatively high lignin content of >5%, KW will result in relatively low specific biogas yield (SBY) of app. 400-500 LN kg-1 of DM.
3) Given that the slurry consists of app. 5% DM, it adds another 0.25 kg (= 5 kg x 0.05) to the containers. This biomass source has usually a very high SBY of app. 850 LN kg-1 of DM (based on results of Triolo et al. 2011, see attached link below).
4) Adding these information to the basic equation, I guess you are looking for:
BYTOTAL = BYKW + BYINOCULUM
BYTOTAL = (KW fresh matter x DM content of KW) x SBYKW + (inoculum fresh matter x DM content of inoculum) x SBYINOCULUM
leads to:
BYTOTAL = 0.25 kg  x 400 LN kg-1 of DMKW + 0.25 kg x 850 LN kg-1 of DMINOCULUM = 100 L + 212.5 L = 312.5 L
5) The SBY of less lignified biomass with relatively high proportions of DM of water soluble sugars, hemicellulose can also reach BYs between 800 and 1000 LN kg-1 of DM. This would remarkably change the outcome of the equation:
BYTOTAL = 0.25 kg x 900 LN kg-1 of DMKW + 0.25 kg x 850 LN kg-1 of DMINOCULUM = 225 L + 212.5 L = 437,5 L
6) Thus, the biogas yield of 1 kg kitchen waste could somewhat range between 100 and 225 LN. The total biogas yield of both waste and inoculum together would be much higher ranging from 300 to 450 LN. To avoid biogas production from the inoculum, I would suggest to deposite the inoculum long enough before the experiment until there is no further notable biogas production from it. Then start the experiment.
I hope, these thoughts could help you. Kind regards, M.v.Cossel
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I'm using Carbon electrode for both anode and cathode to treat stabilize landfill leachate for removal of COD. If i want to calculate operation cost  do i need to measure weight of electrodes before and after EC treatment, because only electrical energy and electrode consumption will be accounted. electricity will account kwh/kg COD removed and electrode consumption in kg. anyone can provide details regarding this issue. thanks in advance!
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Dear Borislav Malinovic
Dear Md. Nuralam Hossain
the sacrificial elelctrode in EC process should be selected of iron or aluminum but not graphite which releases cations to be reacted with hydroxide ions produced at the cathode. note that the cathode may be graphite or st. st. the result is the formation of fog material that has the ability for adsorption pollutants.
pls see the attached file
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(in digestion of wastewater treatment plants sludge)
 thanks in advance.
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General answer is impossible. Optimum mixing depends upon geometry of an anaerobic digestor and on other technical parameters.
Regards   Vit
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Between mechanical, thermal, Chemical, irradiational and Biological technology, which is more effective in the treatment of medical waste: I will be sincerely greatful if reasons are added to ease my selection method.
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Dear Ugya AY
Greetings
During the selection of treatment alternatives for health-care waste (HCWs), decision makers usually consider different criteria and sub-criteria for optimal decisions.
There are many options for the treatment and disposal of medical waste. Some work best in large facilities appropriate to major hospitals or centralized facilities, and others are best for low to middle-income countries, small facilities and resource constrained settings. The first step in any waste management is to minimize waste and to ensure that it is properly segregated at source.
My latest paper was about the assessment and selection of the best infectious health-care waste treatment alternative. We used the sustainability assessment of technology (SAT) methodology which was developed by the
International Environmental Technology Center of the United Nations Environment Program (IETC-UNEP). The focus of this methodology is both on the process and outcome, with an interest towards informed and participatory decision-making.
Our paper is attached for your consideration.
Also you can find our paper from my homepage and from links below:
Hope these are helpful
Best Regards,
Ata
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do you think that adding a carbon additives in to the EGSB will enhance the activity of the reactor and eventually increase the biogas production?
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Coke generated in any refinery has few properties and based on that it is utilized further.
One of the properties is HGI which is easily predicted, but other property BWI takes some time and as per requirement basis.
Is it possible to relate a corelation between HGI of Coke Vs BWI of coke?
Any source or available literature will surely help in this matter.
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Hello,
I'm looking for a feasible industrial application to treat DENIM effluent and remove dyes (indigo and black sulfur).
Biological treatment are not good for vat days removal...
Many Advanced Oxidation Processes are able to remove recalcitrant dyes but they are too much expensive...
Any idea? any experience in full-scale application? 
thanks!!
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We have several full-scale case studies where ozone was used to removed various dyes from textile plant effluent.  Ozone is not technically an AOP and is much less expensive compared to AOP's and chemical removal using coagulants and flocculants.  I agree with Mohamed that biological is best for pretreatment prior to chemical oxidation.  If you have a vat or batch process perhaps it is possible to use SBR or MBBR.
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Dear All,
Could any one help me and tell me how can I get a Boric acid waste in the UK, please?
It is a type of radioactive waste.
Many Thanks,
Manar
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Thank you for the information
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I am studying the pyrolysis of food waste in Macau. I need the data of  the percentage of fly ash against the food waste being incinerated in direct incineration? The food wastes are collected from restaurant, food stalls food centers. 
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Ahmad is right and this because the entire composition of "food waste" is so versatile that you can not work with over thump data!
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In recent years, becoming a popular new organic fertilizer, which is obtained as a product of anaerobic treatment (fermentation) of various wastes. In various countries it is called differently -effluent, digestate... I am interested in information about the efficiency of this fertilizers for different cultures.
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I feel farmyard manure with a stable C:N ratio...
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Is there any feasible method to assess and gauge the odorous gases that are emitted from the sewage or waste water treatment plants? 
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Yes, there are different methods:
- online sensors
- bag sampling combined with lab analyses (odour concentration and/or odour compounds)
- field olfactometry
- nuisance surveys
- emission rates assessment
- impact assessment (incl. dispersion modeling)
I can help you further with this if you wish.
Kind regards,
Bart Kraakman
Principal Technologist
Regional Technology leader - Air Quality and Odour Control ANZ
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I am collecting information about copper refineries in the world and the different costs they have, as well as the efficiency of their processes and regulation of greenhouse gas emissions.
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Dear Gino,
Please see the below given link.
Regards
Krishna
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I have gone through many methods for Leachate Treatment, However i am more interested in a the treatment of Leachate Generated at a Common Hazardous Waste Treatment Storage and Disposal facility
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Dear Sharma,
The  properties of your leachate would inform the type of treatment that you could opt for.  Advanced oxidation processes (Fenton oxidation, photocatalysis, electro-oxidation, etc) could be excellent options for hazardous leachate. Again, the objective of the treatment needs to be defined. 
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Would anyone please suggest deinking methods for recycled papers??
Thank you very much for your advice
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Since the concept of integrated waste management (IWM) highlights that waste management systems are comprised of interconnected functions  Waste management systems depend on the successful interaction and integration of a diverse range of activities, processes, equipment, and people. Many times when changes are made, they are added to an existing waste management system in a “bolt-on” approach This approach will often create additional costs resulting in greater environmental burdens and inefficiencies even if the materials are being processed in a more environmentally-friendly manner. Using an IWM a new system can be formed which considers all of the elements of the system and the interrelations between them.
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Dear Osama Abdelgawad,
Please see the below given link
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In the middle of last century, the disposal of solid waste in sanitary landfills had no form of legislation to regulate the way in which it occurred. At the beginning of the twenty-first century, most first world countries implemented legal measures and these landfills began to be sealed. However, most of the damage was already done, particularly at the level of soil and groundwater contamination. In this partucularly situation, the main problems are the registration of alkaline pH level, high conductivity, high concentration of chlorides, sulfates, bicarbonates and aluminum. How to fix this situation or reverse this trend??
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Dear Carlos,
For some basic insights you may kindly have a look at this link:
Regards
 Krishna
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 we are using a pot with a capacity which is put in cold water, so that flower streams are turned into liquid. We Heat the copper pot for rosewater production.The waste collected at the bottom of the pot, which is called “bongol”, is used to feed livestock and is also dried to be used as fuel in winter or as fertilizer for gardens. and too much water remains. how can I reuse this water and not waste it?
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For production of rose water, if you are using hydrodistilation method, the rose refuse can be mixed in animal feed. Water with dilution can be used to irrigate potted plants.
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I'm currently working on the activated carbon production from industrial waste (petcoke from refinery) via carbon dioxide activation at high temperature (> 800oC) for 1hr. I've realized that upon activation process, the petcoke (powder form) is hardened.
What could be the reason and is there any good technique that can be applied to convert petcoke via CO2 (physical) activation? Through literatures, current work focuses on petcoke conversion via KOH activation.
Thanks.
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Cokes  reacted with CO2  in the temperature range of 800-900 °C. During the reaction, the compositional change of product gases were measured by quadruple mass spectrometry (QMS) for evaluating the gasification rate. Image analysis was carried out to measure the porosity according to the distance from the coke surface.
The reverse Boudouard reaction C+CO2  = 2CO
This C(O) becomes stable with the furnace conditions gradually and starts to inhibit the reaction by blocking active sites of the carbon species,
C(O) = C-O [reversible process];
There is also a proposition that C(O) may be decomposed by leaving the surface of the carbon species as CO:
C(O) = CO.
This process of 'gasification' develops porosity by removing carbon atoms. The purpose of using CO2 during activation is to extract carbon atoms from the structure of the carbon species/compounds being produced/experimented
This is one of the methods to produce active carbon. It is active because it can adsorb a lot due to its great surface area (say, from 100 to 2000 m2/g). This process is named ACTIVATION. You can also do it with other oxidizing agents such as H2O or O2 too. Tensile strength of cokes was strongly affected by their porosity distribution. The porosity at the surface of coke gasified with CO2 indicated low values due to its low reactivity, which resulted in the intraparticle reaction to diffuse into the pores at low temperatures while the coke gasified with H2O showed the tendency to react with the coke at the surface.
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I have agro wastes in lab which has to be converted to biochar. I am seeking advice on how to successfully carry out pyrolysis at 650 degree C in a muffle furnace. I am using Alumina crucible with alumina lid for charring the plant material. What are some ways by which small amount of oxygen which may enter inside the crucible can be avoided to enter inside?
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The muffle furnace is designed in such a way that it does not allow inflow of air/oxygen. Aside from the oxygen that may be trapped in your container when filling it with the sample, which is should be quite negligible since you are using a small sample, then you should not worry so much about the oxygen 
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Stedman had a design that took the solids off ahead of digestion and converted the removed solids to a fuel source. I liked this process as it pulled out a lot of material, which if it had gone through bacterial digestion, would have been converted into solution which is more difficult to control. Is anyone working along these lines? I ask because a lot of the pharmaceuticals are broken into more toxic daughter products either by bacterial digestion or later oxidative processes, and many are mitochondrial toxins (MT). Thus using the effluent as an irrigation source or drinking water augmentation sees these MTs bioaccumulating in irrigated crops or being chronically delivered with drinking water.  Thanks------------Edo
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The plant is a typical municipal secondary plant treating 8 million gallons per day, and equipped with a 4.3 million gallons per day Tertiary Treatment for recycled water. The idea is to suggest sending a cleaner influent through plant by removal of solids up front. This would substantially diminish bacterial digestion of solids, including pharmaceuticals. Plant is down-gradient from level 4 teaching hospital and surrounding labs and other clinical facilities. Recycled water is slated to be augment source for groundwater recharge. A cleaner end-influent would presumably make the raw stock becoming recycled water less of a hazard and easier on equipment.
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Dear Sir/Madam,
I am using immersion heater and it has specs(3kw 418v)and it does have thermostat which can be controled temperature from 30 to 110 degree.
I am using this heater to typical drum (200 ltrs steel drum), the drum containes waste cooking oil (solid state). As you can see the dirty drawing( sorry about my hand drawing), most of oil melted but some of oil is still in solid state.
I calculated that the oil should have completely melt in 3hours at 15degree (atmospheric pressure) but even after 7 hours, still in same state like the hand drawing.I set the temperature of heater @ 80degree, thus the heater turned off at 75~76degree( its what the manufacturer says) automatically.
Does anyone can let me know the solution of even the reason for this..
Please let me know sirs..
best regards,
Kim
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You need to stir also or move the heater to different places in the drum. Convection of heat is (evidently) not sufficient.
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I have an experiment using IR where jet fuel is heated up to different temperature and analyzed with FTIR. My question is, what kind of chemicals you can use to kill the jet fuel effluent off the FTIR? I'm picturing flowing the effluent out of the IR through a bubbler than contains some kind of a liquid to scrub off the jet fuel.
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Ice or Water spray
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I want to measure the dissolved organic carbon and particulate organic carbon in water sample. Anybody know any institutes or laboratories that provide these services for outside samples.
Thank you in advance
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For the measurement of Dissolved Organic Carban ( DOC) and Particulate Organic Carban ( POC ), kindly contact :
Director, National Environmental Engineering Research Institute, Nagpur.
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Dear folks,
I'm working on building a bench scale reactor and I would need your help with a matter. For this reactor I would like to use a pump able to pump a slurry containing particles that might be a little bit sticky. The slurry I want to pump in will be a mixture of food waste, sewage sludge and crop waste grind and diluted together with water so the final solid concentration will be about 80-90 g/L. The flow that I'm envisaging to use will be between 3 to 6 L/d.
Do you have any suggestion regarding this aspect?
Thank you very much.
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Have you tried bucket elevators?. I think they could work.
For example:
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The incineration plant treat the mixed municipal waste and food waste (including wet market waste and restaurant waste).
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Food waste contains mineral elements, so after combustion you can always obtain a bit of ash. Some part of it you can find as a fly ash. Its quantity depends on combustion conditions and construction of combustion unit.
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i am phD student , i want to find  the best change in design of conventional bio-scrubber to reach to high efficiency for removal volatile organic carbon  (VOC)  emitted from oil refinery
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Mist scrubbers are very efficient in collecting volatile organic compounds found in the effluent of industrial gas streams. Mist scrubber technology has been used very sucessfully in controlling the odors escaping from industrial production process. Mist scrubbing has proven to be a simple, practical technology over the past 18 years. Now, by adapting the technology, other new applications are possible. QUAD's mist scrubbing technology is very effective in removing both low-concentration odors and VOCs. QUAD mist scrubbing will cost one-fifth or less in life-cycle cost.
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I am a WASH and urban development specialist living and working in East Africa. I am attempting to scope out “temporary” solutions to sanitation and waste challenges in large unplanned settlements in Dar es Salaam and Nairobi and am looking to receive feedback/critique/advice. I understand these solutions do not sound politically/technologically correct, but with local resource limitations, I seek to identify low-cost, non-motorised and intuitive methods that can be implemented quickly on the ground.
I am interested in what role EM-1/Bokashi could play, purely as a waste management solution in respect of both organic (market waste) and liquid waste (faecal sludge). The purpose is NOT to produce compost, but to mitigate odour, pests and the transmission of disease.
1. Could EM-1/Bokashi bran be added to large municipal containers (e.g. skips) to mitigate odour, pests, disease transmission? 2.mCould EM-1/Bokashi bran be dropped into pit latrines to mitigate odour, pests, disease transmission?
2. Could EM-1/Bokashi bran be dropped into pit latrines to mitigate odour, pests, disease transmission?
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EFFECTIVE MICROORGANISMS (EM)
EM is a brown colour liquid concentrate containing a consortium of beneficial microbes and acts as soil conditioner as well as a microbial inoculant. It is produced from cultivation of over 80 strains of beneficial microorganisms, which are collected from the natural environment. Over 90 countries are using this technology successfully today.
EM stock solution mainly consists of lactobacillus, photosynthetic bacteria, yeast and ray fungi. The microorganisms are not imported or genetically engineered. EM includes both aerobic and anaerobic species of microorganisms which co-exist in an environment of around 3.5 pH. EM is used in agriculture, animal husbandry, aquaculture, waste water & solid waste management to increase the quantity and to improve the quality of products and the treating of certain poluting ellements.  It has been observed that increasing the dosage of EM to make compost also increased the nutrient level.
EM Bokashi
Bokashi is rich a fermented compost, which can be made as ‘aerobic’ (allowing air contact) or ‘anaerobic’ (without air contact), depending on the process used. Bokashi is a strong organic manure with beneficial effects towards the soil. Aerobic Bokashi can be made on a large scale. As the temperature will rise (up to 40 – 50 °C) during the process of composting it has to be controlled (e.a. by aeriation) to maintain energy.
Anaerobic Bokashi: The process is a bit more demanding but it is superior to aerobic Bokashi as it has more nutrients. It is important to note the quantitys beeing applied of this Bokashi are much lower.
Ingredients for making Bokashi
Organic Material: Rice, corn or wheat bran, maize flour, rice or bean husk, rice, wheat or corn straw, any oil seed cake, cotton seed cake, press mud, chopped crop residue or weeds, saw dust, dried sea weed, coconut fiber and husk, post harvest residue etc. Animal Residues: Fish or bone meal, animal dung, crab shell, waste from meat-industry.
It is best to have a balance between plant and animal material in the ratio of 2:1 and to have a mix of many different types of organic ingredient. A typical Bokashi contains the following: Rice Bran: Oil cake: Fish/ Bone Meal: Water: Molasses: EM in the ratio of 2.5kg: 2.5kg: 2.5kg: 150 ml: 150 ml: 150ml by volume. The quantity of water can be altered depending on the moisture content of the ingredients used. The material should be moist without drainage. It is recommended that at least 10-15% rice bran should be present in all Bokashi recipes.
EM in action
Current research indicates that EM cultures can suppress soil-borne pathogens, accelerate the decomposition of organic wastes, increase the availability of mineral nutrients and useful organic compounds to plants, enhance the activities of beneficial micro-organisms, e.g., mycorrhizae, nitrogen fixing bacteria, and reduce the need for chemical fertilisers and pesticides. EM helps to increase beneficial soil micro-organisms and supression of harmful ones.
As a compost application
Apply to the compost heap to reduce troublesome odours and flies as well as improving the compost process and quality. Preferably spray on with a hand sprayer to prevent over wetting the compost heap and apply at each addition of fresh material if possible.
How to produce Anaerobic Bokashi?
Mix rice-bran, oil cake and fish/bone meal thoroughly. Dissolve molasses in water (1:100) and add EM to the solution. Pour this mixture on the dry ingredients and mix well. Please ensure that no lumps are left after mixing. Place this mixture in a polythene bag or airtight container and make it airtight. Release all air from the bag, place the packed bag in another polythene bag and again make it airtight. Store in a dark place. Bokashi is ready in 4 - 5 days in summer and 7 - 8 days in winter under tropical conditions (in other regions store at 24 – 26 °C). It will smell sweet and fermented when ready. Anaerobic Bokashi should be used soon after preparation. For storage, spread it on soil and dry it in the shadow. When dry, it can be stored in polythene bags. Keep the Bokashi save from rodents and other pests.
How to produce Aerobic Bokashi:
The ingredients and method of mixing is similar to anaerobic Bokashi. Spread the mix on soil and cover it with gunny (jute) bags, straw, mat or similar matter to keep it from rain. The temperature rises rapidly but is controlled at 25°-35° C by turning the mix upside down. This may have to be done 3 or 4 times. Bokashi is ready in 4 - 5 days. Store like anaerobic Bokashi. Application of any kind of Bokashi: Broadcast Bokashi on the soil at 600 kg per acre or 250 gms/ m2 till or plough the soil so that the Bokashi is covered with 5-8 cms of soil. Use mulch to cover the soil thereafter Caution: No seed or sapling to be sown or planted for 5-10 days after application of Bokashi. (The more you give - the longer you wait)
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I'm interested in recent studies that compare various e-waste regulations around the world?  This could include comparisons against a set range of criteria, critical analysis, pros and cons and/or recycling performance?
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There are a number of parameters on which the performance of the various disposal solutions available can be analyzed and compared. But, the most useful parameters work out to be environmental impact, disposal capacity, and cost and disposal time.
Electronic waste or e-waste describes discarded electrical or electronic devices. Used electronics which are destined for reuse, resale, salvage, recycling or disposal are also considered e-waste. Informal processing of e-waste in developing countries can lead to adverse human health effects and environmental pollution.
Electronic scrap components, such as CPUs, contain potentially harmful components such as lead, cadmium, beryllium, or brominated flame retardants. Recycling and disposal of e-waste may involve significant risk to workers and communities in developed countries and great care must be taken to avoid unsafe exposure in recycling operations and leaking of materials such as heavy metals from landfill sand incinerator ashes.
Growth in technology enhances need and utilization of electronic and electrical equipment’s (EEE) everywhere in the world. As a result, e-waste acquires a large share in the conventional solid waste stream. Limited recycling solutions available pushes the need for e-waste disposal solutions. the increasing e-waste pie in solid waste. Various disposal solutions available for ewaste are presented in the paper. A comparison of various disposal solutions done on the basis of parameters like disposal capacity, harm to the environment and its resources, cost and time constraints analysis. Landfill dumping solution is most accepted, proving out to be best among all solutions by acting as a reserve to be recovered in future with the development of more recycling facilities.
Recycling Solutions,  Disposal Solutions
E-WASTE DISPOSAL SOLUTIONS
Thermal treatment disposal(Open Burning, Incineration)Dumping disposal(Open dumps, Conventional Landfill dumping, Sanitary Landfill dumping, Deep well disposal)
Environmental Impact: Open burning of the e-waste is associated with harmful emissions comprising of dioxins and furans which cause a great threat to the environment. In comparison, incineration fumes are controllable with the help of chimneys. In open dumping and conventional landfill dumping, leaching of toxic material takes place. Although, the rate of leaching is very slow but the leach ate can potentially give birth to formation of toxic byproducts with time . Therefore, looking into the environmental concern, sanitary landfill disposal solution causes minimum harm to the biotic life. Disposal Capacity: Open burning and incineration processes are generally adopted for small scale disposal whereas for large junk of waste, landfill dumping serves as an alternative . Cost and Disposal time: Cost of development of infrastructure for incineration is many folds as compared with that of landfill construction. But, the time of disposal that takes place in dumping is more in contrast with incineration .
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I have a dried sewage sample that was mixed with distilled water.  After shaking for 24 hours, the solids were filtered out and the liquid retained.
I tested the liquid for ortho-phosphates.  But in order to do this, I had to add a drop of sulfuric acid as a preservative.  When I was done with the phosphate determination, I had a lot of sample left over and decided to evaporate off the liquid to measure the Total Dissolved Solids. 
Here is the fun bit...
I added a  drop of acid to the filtrate, and then placed the sample in an oven where the water to evaporated off.  The remaining solids had a distinct greasy texture.  It appeared that the solids had curdled and trapped droplets of water inside.
but...
If I did not add the drop of acid and placed the sample in the oven, the resulting solid was dry and powdery.
An IR analysis of the solids suggests that I have some sort of polysaccharide.  So is this behavior consistent with polysaccharides?  Proteins might also be present and they certainly would behave in that fashion.
I do have a GC/MS and several LC/MS instruments, but my colleagues would not appreciate me running this solution on our departmental shared instruments without first knowing what is in it.  (Don't ask me how I know this.) 
Once I have a good idea of what might be in the solution I can do the LC/MS analysis.
Thank you.
Kevin
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Did not say if it was dried raw sewage sludge or dried waste activated sludge ( any polymers or floccing chemical used) mixed with sulphuric acid? Starting with a 1921 book, see some books, paper and patents below:
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The future of humankind will heavily depend on successful learning and implementing sustainable lifestyles. Maintaining the presently practiced lifestyles with increasing drive for economic growth and production, consumerism, dominating linear supply systems and global resource and product transactions may counteract the envisioned sustainability. As one concept for change, the establishment of circular economy (also called Green Economy) is praised. But is this approach valid in the context of developing countries? The Worldbank (2012, Hoornweg & Bhada-Tata) estimates that the global solid waste generation will increase from 1,3 Billion tons in 2012 to 2,2 Billion tons by 2025. "Cloosing the loops" for municipal solid waste management alone would mean to successfully tackle +1 Billion tons additional solid waste every year in the next decade. But reality is that public waste management services are too low to tackle the now 1,3 Billion tons per annum, especially in low income countries. In parallel, other waste streams from sanitation systems as well as food and agri-wastes (manures!) need to be addressed. Most developing countries are in the process to increase 'access to toilets' to lessen open defecation (as more than 800 Million people still practice this on the planet at present). However, central sewerage systems may be available in developed countries but may not be affordable in most developing countries for decades to come. Most developing countries provide onsite sanitation systems where sludge from toilet use is contained and stored. However, sludges from tank cleaning are mostly not treated and reused properly, but often disposed in an uncontrolled manner. In fact, so far, public waste management services in developing countries mean to collect and dispose waste only whereas waste treatment facilities and successful recycling businesses are hardly developed. In the contrary, material recovery mostly depends only on the informal sector, which means poor people that make a living by material recovery in an unorganized manner pick some resuseable waste fractions 'at source, from collection trucks, or by scavaging at dumpsites' (often under un-human work conditions). Development in most cities in the developing countries does not happen in a planned manner, but often responds on tackling priority needs. Besides, severe barriers such as lacking funds, local political situation, lack of know how and legal framework and institutional support as well as low private sector involvement and interest to invest hinder system enhancements. In this context the question arises: What are the most promising strategies and developing steps we should promote to counteract the presently worsening situation along 'all anthropogenic waste streams'?
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Dear Johannes,
I actually wonder if what the developed countries have needed to design and name as a concept "circular economy" is not existing already (and has never stopped existing) on a daily basis in developing countries: have you seen in these countries how many people rely on over age equipment repaired and fixed again and again and how many people live from the collection and treatment of "waste" (= resource)? I think the developed countries are facing the issue because they have lived well above the threshold of reasonable resource consumption for too long, disrupting the basic common sense, hence the need to "invent" a concept to just come back to what we were doing well 3 generations before now. On the other hand, developing countries that have not yet reached the point of cradle to grave linear economy, are still living with the model of cradle to cradle economy that developed countries are now struggling to re-implement. To a certain point, developing countries well might be far more efficient and lessons giver to developed counties with this regard, and have less to unlearn and relearn than developed countries.
Rgds,
Juliette
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The most efficient , the cheapest and the most enduring .
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In the 3R Waste Management Strategy (reduce, reuse, recycle), "reduce" is considered the best way of waste management. Then, what is the best and most effective way in reducing waste, especially in the urban area? 
From my point of view, the best and often the easiest way to reduce the amount of waste is to take steps to generate less waste in the first place. Very small and simple changes in the way of living can have dramatic effects on how much waste to be generated. We, as a consumer and urban dweller, have considerable power to reduce the amount of waste going to land fill by choosing to buy products that use less packaging or are packaged in recyclable materials.
It is also worth remembering that although recycling an item of waste is better than disposing of it in the normal trash, a lot of energy is consumed for both the recycling process and the transportation of the waste to and from the recycling center. Any steps you make that reduce or eliminate the use of an item you would normally recycle or throw away will have a significant positive impact on the environment. Choosing products that are reusable and long lasting instead of single-use disposable products will save a lot of waste and also save money over the long term.
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I need to investigates methods for ion and volatile removal from waste water, in order to choice the cheapest and most effective one. Thanks indeed 
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Dear
Caser Ghaafar Abdel, Hi, It is related to you, Do you require to use the treated wastewater for reuse or no? If your reply is positive, what quality, for irrigation, recharge of underground water, reuse for washing in industry, high quality for drinking water or no, you just to treat for dischage to river or sea or underground or other uses.
Usually for cheap treatment you can use an ABR system combined with Anaerobic filter and following that subsurface wetland or a natural system.
Best regard 
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FTP Dust is the byproduct or waste from steel production industry
it is fine powder with brown color and have pH more than 12.5 and contains trace elements like Selenium and zinc.
being highly alkaline it must be stabilized before land filling what would be the best cost effective process to do that .
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Alternative to citric acid may be a solution of carbonic acid (CO2 + water) effective and low cost 
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Recycled products or products that contain secondary raw materials can make up a core constituent of a large number of consumer and industrial products. Governments and industry have allowed the development of recycling systems for certain products in view to provide a comparatively lower level of environmental load compared to virgin materials, for example renewable energies (e.g. as biogas from waste) instead of fossil fuels. E-waste recycling is on the agenda, but solved?
Although recycled products may be environmentally preferable based on reduced demand for virgin materials and reduced amounts of waste going to landfills. But many recycling products fail in the longer run due to lack of markets or deteriorating markets, other reasons or negative customers responses a) based on disadvantages of the recycling product or b) due to the customer suspicion that such products may have ‘less quality or value’ and c) because they are subsidized.
Also many companies, agencies etc promote certain recycling products and offer ‘quality standards/logos’ it can be witnessed that many recycling initiatives are ‘more risky and less stable’ if compared with traditional production methods or even need to be subsidized in order to be maintained over longer time periods (e.g. compost).
If these assumptions are valid which criteria and parameters are crucial to assess validity of recycling products in an integrated manner before market introduction?
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Dear Johannes,
There is as far as I know not such a holistic approach to waste management assessment. There are pieces of the puzzle lying around.But your question inspires me to add a paragraph to a technical report (on the technical description of packaging material recycling chains) that I currently writing on this topic. I will send you a copy when I am done.
The research field of waste management is much more complex than most people think. Many stakeholders have invested greatly in waste management and are keen to safeguard their investments and the complexity offers them the opportunity to tell the story they want. That is why there are so many biased reports on waste management. That is also why you will not find the assessment method you are looking for.
All the packaging material recycling schemes suffer from their own unique drawbacks.
Glass packaging recycling is relative circular in the sense that about 80% of the packaging glass is reused in packaging glass and the rest in foam glass and soem waste, polish sand etc. But this systems suffers from non-optimal collection responses. And the need for recycled flat-glass as input to keep the elemental pollution sufficiently low.
Metal packaging recycling suffers from its value in the sense that is almost impossible to find out where the metals end up. The ferrous metals are most likely used in local foundries and find their application is a whole array of applications: construction, rails, machines, etc. The non-ferrous metal packages (Aluminium) end up in in an aluminium alloy that is relatively rich in Silicium and can therefore best be used for casting engine blocks. So high responses through mechanical recovery and a whole lot of application, but typical outside the packaging market.
Paper & board recycling is a cascadar recycling system with a renewable input to replenish the lost fibres. From a technical yield point of view it operates good. But from a quality point of view, there are substantial challenges for using it in packaging in a food safe manner. 
Plastic packaging recycling is also mostly a cascadar recycling system. Only PET bottle recycling can be operated in a true circular manner. The chemical nature of polyolefines is such that circular packaging recycling is near impossible. So most is cascadarly recycled into various utensils. There is a large market for these recycled plastics, but the costs for collection and sorting are high. The local industry has still to adapt to the presence of this material and the virgin plastic producers are not involved yet.
Personally, I regard the era that we are living in as a transition era. It will take a lot of time and effort to transform our economies to more sustainable economies and we will have our ups and downs in the process. There is no simple cheap solution for everything yet. The environmental benefits are potentially large and it will cost us a lot of money.
Regarding your landfill example, you have to accept the biological activity and the formation of GHG emissions and polluted percolate water. Both have to be captured and cleaned. This seldom happens efficiently and hence the environmental drawbacks are substantial. So, yes all systems have their own drawbacks on different parameters... I hope this helps you forward.
Greetings
Ulphard
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On the list of top ten things we wished had never been invented, plastic is the no.1. Each year roughly 8 million tons of plastic has to be dumped into oceans. On the other hand, each year enormous quantities of radioactive waste which contain the most dangerous materials are created by nuclear power generation. Both types of pollution are notorious for the long-lasting global effects.
In Chinese, there is a strategy which is translated as "To set a thief to catch a thief.", or "To cure poisoning by poison". So, there might be a way to "control (one type of) pollution by (another type of) pollution".
It is well known that radiation or high energy beams are used to decompose polymers. However, I don't know how effective those radioactive waste materials are for degradation of polymers. Suppose they are effective, then deposit of nuclear waste surrounded by plastic waste might be a solution to both types of pollution.
There is still another way --  to design new polymers that can be easily decomposed by radiation.
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Sergei,
Thank you so much for the links. This is so exciting. I havn't look at them yet. There is a will and there is a way. My thinking is that we should develop radiation-sensitve plastic materials, and hopefully there is a chain reaction of degradation in the plastic waste triggered by radiation. Of course if you look in all details there are so many challenges, but who knows? There might be a genius who find a way to save the earth!
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Cheese whey is generated in large volumes (450 litres of whey generated for every 500 litres of milk used in cheese making) in cheese and diary farms. It is highly biodegradable and saline waste effluent. Literature displays active investigations in treatment and reuse of treated wastewaters but they don't look like an economic option for scale up. Please give your views..!!
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Jai, Have you seen this one; It exactly talks of your opint that cheese whey has been treated so far but not volaorized and they give some options- Cheese whey management: A review, http://www.sciencedirect.com/science/article/pii/S0301479712002769
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The level of sulfate present in the construction and demolition debris tends to be higher than what is permitted by the European norms. In order to reuse these wastes the levels of sulfate must be reduced. I would like to know what could be the cheapest and most effective method to do so.
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I would look into lime as a possibility.  Lime is relatively inexpensive and probably will work.  I went on the internet to confirm and lucked out, found this for you.  I did not read.  There are also sulfate reducing bacteria and they work in wetlands and can convert ionic mercury to methyl mercury, the toxic form.  I have also recommended liming of rifle ranges near riparian areas as this would tend to hold the lead instead of moving into groundwater.
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Equations
Previous studies
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Siltation will increase the evocation by two ways  by reducing the storage capacity  ( increasing the surface area and by absorbing higher solar  radiation
The first effect will be significant  only for heavy siltation the second  if the turbidity is high 
You can study both effects by lab experiment by assessing the  S'S and turbidity   levels and  corelating  to lake or pond topography. 
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Development of a new absorbing material.
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Adsorption, coagulation , and Oxidation were found very efficient in removing color and organic compounds from industrial waste water particularly textile waste water. each process has its futures and some drawback. 
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I'm trying to design a research proposal on effect of leachate from municipal wastes on some organisms
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Dear Andem,
the following publications may be helpful for writing your proposal:
In addition, attached please find another 4 publications.
Rafik
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