Low emissions, high working capacity adsorbent and canister system
The present description provides high working capacity adsorbents with low DBL bleed emission performance properties that allows the design of evaporative fuel emission control systems that are lower cost, simpler and more compact than those possible by prior art. Emission control canister systems comprising the adsorbent material demonstrate a relatively high gasoline working capacity, and low emissions.
1. An evaporative emission control canister system comprising:
at least one adsorbent volume, and including a shaped adsorbent material comprising an admixture of a binder and an activated adsorbent powder having a butane activity (pBACT) of at least about 50 g/100 g, derived by grinding an activated adsorbent precursor, wherein the admixture is shaped into a form,
wherein the shaped adsorbent material has an ASTM BWC of at least 13 g/dL, and at least one of: (i) a ratio of pore volumes of 0.05-1 micron to 0.05-100 microns that is greater than about 80%, (ii) a ratio of pore volumes of 0.05-0.5 micron to 0.05-100 microns that is greater than about 50%, or (iii) a combination thereof.
2. The evaporative emission control canister system of claim 1 , wherein the canister system comprises at least one fuel-side adsorbent volume and at least one vent-side adsorbent volume, wherein at least one of the at least one fuel-side adsorbent volumes or at least one vent-side adsorbent volumes or a combination thereof includes the shaped adsorbent material of claim 1 .
3. The evaporative emission control canister system of claim 1 , wherein the shaped adsorbent material has two-day diurnal breathing loss (DBL) emissions of 100 mg or less at 315 liters of purge applied after a 40 g/hr butane loading step as determined in a Defined Canister by the 2012 California Bleed Emissions Test Procedure (BETP).
4. The evaporative emission control canister system of claim 1 , wherein the system has two-day diurnal breathing loss (DBL) emissions of less than 100 mg when tested by China 6 Type Test Procedure.
5. The evaporative emission control canister system of claim 1 , wherein the activated adsorbent precursor is an activated carbon precursor.
6. The evaporative emission control canister system of claim 1 , wherein the binder comprises at least one of an organic binder, an inorganic binder or both.
7. The evaporative emission control canister system of claim 6 , wherein the organic binder is at least one of carboxymethyl cellulose (CMC), a synthetic organic binder or both.
8. The evaporative emission control canister system of claim 6 , wherein the inorganic binder is a clay.
9. The evaporative emission control canister system of claim 5 , wherein the activated carbon precursor is derived from at least one of wood, wood dust, wood flour, cotton linters, peat, coal, coconut, lignite, carbohydrates, petroleum pitch, petroleum coke, coal tar pitch, fruit pits, fruit stones, nut shells, nut pits, sawdust, palm, vegetables, a synthetic polymer, natural polymer, lignocellulosic material, or a combination thereof.
10. The evaporative emission control canister system of claim 1 , wherein the form is selected from a pellet, granule, sphere, honeycomb, monolith, cylinder, particulate, hollow-cylinder, star, twisted spiral, asterisk, configured ribbon, or a combination thereof.
11. The evaporative emission control canister system of claim 1 , wherein the canister system comprises at least one vent-side adsorptive volume having at least one of: (i) an incremental adsorption capacity at 25° C. of from 4 grams n-butane/L to less than 35 grams n-butane/L between vapor concentrations of 5 vol % and 50 vol % n-butane, (ii) an effective BWC of less than 3 g/dL, (iii) a g-total BWC of less than 6 grams, or (iv) a combination thereof.
12. The evaporative emission control canister system of claim 1 , wherein the canister system comprises at least one fuel-side adsorptive volume having an incremental adsorption capacity at 25° C. of greater than 35 grams n-butane/L between vapor concentrations of 5 vol % and 50 vol % n-butane.
13. The evaporative emission control canister system of claim 1 , wherein the system has two-day diurnal breathing loss (DBL) emissions of 20 mg or less with no more than 315 liters of purge applied after a 40 g/hr butane loading step as determined by the 2012 California Bleed Emissions Test Procedure (BETP).
14. The evaporative emission control canister system of claim 1 , wherein the system has two-day diurnal breathing loss (DBL) emissions of 20 mg or less with no more than 150 BV of purge applied after a 40 g/hr butane loading step as determined by the 2012 California Bleed Emissions Test Procedure (BETP).