Process and apparatus for safe disposal of used ionic liquid catalyst
US-9216393-B2 · Dec 22, 2015 · US
US9339806B2 · US · B2
| Field | Value |
|---|---|
| Publication number | US-9339806-B2 |
| Application number | US-201213484245-A |
| Country | US |
| Kind code | B2 |
| Filing date | May 30, 2012 |
| Priority date | Sep 8, 2005 |
| Publication date | May 17, 2016 |
| Grant date | May 17, 2016 |
A practical reading order for non-experts. Skip the full description unless you need deep technical detail.
What the patent document calls the invention.
A short plain-language summary of the technical disclosure.
Who owns or filed the patent and who is credited as inventor.
Filing, priority, publication, and grant dates set the timeline.
The legal scope of protection — read this for what is actually claimed.
Technology tags used to group this patent with similar filings.
Prior art links and similar publications in this corpus.
Official abstract text for this publication.
Industrial waste derived adsorbents were obtained by pyrolysis of sewage sludge, metal sludge, waste oil sludge and tobacco waste in some combination. The materials were used as media to remove hydrogen sulfide at room temperature in the presence of moisture. The initial and exhausted adsorbents after the breakthrough tests were characterized using sorption of nitrogen, thermal analysis, XRD, ICP, and surface pH measurements. Mixing tobacco and sludges result in a strong synergy enhancing the catalytic properties of adsorbents. During pyrolysis new mineral phases are formed as a result of solid state reaction between the components of the sludges. High temperature of pyrolysis is beneficial for the adsorbents due to the enhanced activation of carbonaceous phase and chemical stabilization of inorganic phase. Samples obtained at low temperature are sensitive to water, which deactivates their catalytic centers.
Opening claim text (preview).
I claim: 1. An adsorbent formed by drying waste materials, wherein the improvement comprising: a) a waste material composition, comprising: (i) one of compost or compost materials and sludge; (1) wherein the compost is one of tobacco waste, waste paper, wood char or a combination thereof; (2) wherein the sludge is at least one of waste oil, metal, or municipal sludge; (ii) 20-30% porous organic carbon with incorporated organic nitrogen species; and (iii) 70-80% inorganic matter; b) adsorbent characteristics, wherein; (i) the adsorbent is capable of adsorbing up to about 30% of the adsorbent's weight in hydrogen sulfide; (ii) a surface area of the adsorbent is 10-200 m 2 /g; and (iii) the pH of the adsorbent is between 7-12. 2. The adsorbent of claim 1 , wherein the inorganic matter includes dispersed catalytic oxides. 3. The adsorbent of claim 2 , wherein the catalytic oxides are one or more of copper oxide, zinc oxide, iron oxide, calcium oxide, silica and alumina. 4. The adsorbent of claim 1 , wherein the nitrogen species comprises amine or pyridine groups. 5. The adsorbent of claim 1 , wherein the adsorbent contains micropores and the volume of the micropores is at least 0.03 cm 3 /g. 6. A method of making an adsorbent which comprises the steps of: a) composting tobacco waste, waste paper, wood char or a combination thereof; b) thermally drying at least one of dewatered waste oil or metal sludge; c) mixing the dried sludge and the compost; d) pyrolyzing the mixture at temperatures between 600° C. and 1100° C., comprising the steps of: (i) heating the mixture between 5 and 10° C./minute; (ii) holding the heated mixture between 60 and 90 minutes; and (e) forming an adsorbent, wherein: (i) the adsorbent is capable of adsorbing up to about 30% of the adsorbent's weight in hydrogen sulfide; (ii) a surface area of the adsorbent is 10-200 m 2 /g; and (iii) the pH of the adsorbent is between 7-12. 7. The method of claim 6 , wherein the temperature of pyrolysis is between about 600-700° C. 8. The method of claim 6 , wherein the temperature of pyrolysis is between 900 and 1100° C. 9. A method for producing an adsorbent, comprising the steps of: (a) combining at least one of a waste oil or metal sludge and a compost material comprising at least one of tobacco waste, waste paper and wood char, or a combination thereof, to form a mixture; (b) thermally drying the mixture; (c) pyrolyzing the mixture at a temperature between about 600° C. and 1,100° C.; and (d) forming at least one of wurtzite, ferroan, chalcocite, spinel, feroxyhite, bornite, hibonite, zincite, ankerite, pyrope, perrohotite, chalocopyrite, triolite, fersilicite, sapphirine, maghemite, cohenite, lawsonite, smithsonite, sphalerite, goethite, huntite, anorthite, diaspore, vaterite, lepidirocite, bayerite, moghemite, pyrohotite, hematite, and almandine during the pyrolyzing step.
Porosity, e.g. pore volume · CPC title
with stationary adsorbents {(B01D53/025 takes precedence)} · CPC title
Nitrogen compounds · CPC title
comprising silica · CPC title
being less than 100 m2/g · CPC title
Related publications grouped by family.
Answers are generated from the same data shown on this page.