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Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`IN THE UNITED STATES PATENT AND TRADEMARK OFFICE
`
`Examiner: DIAMOND, ALAND
`
`Group Art Unit: 3991
`
`Confirmation No: 2755
`
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`)
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`In Inter Partes Reexamination of:
`
`BULLET AL.
`
`Reexamination Control No. 95/001,453
`
`Patent No. 7,601,662
`
`Issued: October 13, 2009
`
`For: COPPER CHA
`ZEOLITE CATALYSTS
`Mail Stop Inter Partes Reexam
`Central Reexamination Unit
`Commissioner for Patents
`P.O. Box 1450
`Alexandria, VA 22313-1450
`
`SECOND DECLARATION OF AHMAD MOINI, PH.D., UNDER 37 C.F.R. § 1.132
`
`I, Ahmad Moini, do declare and say as follows:
`
`1. I am a Senior Research Associate for BASF Corporation, the successor in interest to
`
`Engelhard Corporation and BASF Catalysts LLC (BASF), the owner of United States patent number
`
`7,601,662 ("the '662 patent"). I received a B.S. in Chemistry from Eastern Washington University in
`
`1982 and a Ph.D. in Chemistry from Texas A&M University in 1986. I have been a scientist at
`
`BASF Corporation. I am a co-inventor of the subject matter described and claimed in the '662
`
`patent.
`
`2. I have been involved in heterogeneous catalyst research for more than 20 years, first as a
`
`researcher at Mobil Research and Development Corporation, and later at BASF Corporation. I am a
`
`named inventor on 33 granted United States patents, some of which pertain to zeolites for use as
`
`automotive catalysts.
`
`3. I submitted a first declaration in this matter on February 9, 2011. I have been asked to
`
`conduct several experiments to compare the catalytic performance of the catalysts claimed in the
`
`'662 to the performance of catalysts that have been considered the closest prior art in this
`
`reexamination. I have reviewed the '662 patent, the Office Action dated November 16, 2010, the
`
`Action Closing Prosecution dated November 18, 2011, including the documents cited in the actions,
`1
`
`Exhibit 2011.001
`
`

`
`as well as additional documents cited in this second declaration. I have read Dr. Lercher's
`
`Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`declaration and Exhibit C-4.
`
`Dedecek Samples
`
`4.
`
`It is my understanding that the Examiner finds that with respect to the rejections based on
`
`Dedecek in view of Chung, the closest prior art is two examples from Dedecek, one being the natural
`
`CuCHA zeolite having a Cu/Al atomic ratio of 0.38 (the sixth entry in Table 2 on page 66) and other
`
`being the synthetic CuCHA zeolite having a Cu/Al atomic ratio of 0.32 (the eleventh entry in Table
`
`2 on page 66). I have been asked to recreate these examples from the Dedecek reference.
`
`Natural CHA Sample:
`
`5. For the natural CuN atCHA example, the Dedecek reference started with natural chabazite
`
`from North Korea having the chemical composition 63.89% Si02, 17.48% Ah03, 8.37% Fe20 3,
`
`5.15% K20, 3.10% CaO, 1.21 %, MgO, 0.40% Ti02 and 0.39% Na20. However, due to import
`
`restriction under the United States Department of Treasury Office of Foreign Assets Control, we are
`
`not able to obtain natural chabazite samples from North Korea. Accordingly, I obtained a sample of
`
`natural chabazite zeolite sample from a mine in Bowie, Arizona as an indirect comparison to the
`
`CuN atCHA sample in Dedecek. The Bowie sample is comparable to the one from North Korea in
`
`terms of the metal oxides content other than silica or alumina. The chemical composition of the
`
`Bowie sample, determined by X-ray Fluorescence, was 64.74% Si02, 21.54% Ah03, 9.84% Na20,
`
`1.37% Fe20 3,0.93% K20, 0.59% MgO, and other residual components. The primary phase of this
`
`material was determined to be Chabazite, with secondary mineral phases present, as would be
`
`expected by a natural material.
`
`6. Per the example preparation in Dedecek, the CuNatCHA sample was equilibrated three times
`
`with 0.5M NaCl (20 ml of solution per 1 g zeolite) for 2 hours, and a fourth was carried out
`
`overnight. These equilibration times varied from Dedecek' s procedure, but it is understood that, with
`
`this type of alkali equilibration, the key parameter is the number of exchanges rather than the total
`
`exchange time. After the ion exchange, the Na-chabazite was washed with distilled water and dried
`
`at room temperature. The powder from the NaCl treatment was subjected to two Cu acetate
`
`treatments, under the same conditions described in Dedecek et al., Table 2, entry on row 6. The final
`
`product was washed thoroughly with distilled deionized water. Elemental analysis revealed 65.13%
`
`2
`
`Exhibit 2011.002
`
`

`
`Si02, 17.45% Ah03 , 8.91 % CuO, 4.52% Na20, 3.31 % Fe20 3 , 0.66% K20, 0.44% MgO. Based on
`
`Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`these data, the Cu/Al ratio was 0.32.
`
`Synthetic sample:
`
`7. A sample of synthetic Chabazite was synthesized according to the procedure referenced in
`
`Dedecek et al. Zeolite Y (CBV-600) was mixed with KOH solution and reacted at 95°C for 92
`
`hours. The resulting product was washed thoroughly with distilled deionized water. The formation
`
`of Chabazite product was confirmed by XRD.
`
`8. The chabazite powder was subjected to four NaCl equilibrations. The first three treatments
`
`were for two hours, while the fourth was carried out overnight. These equilibration times varied
`
`from Dedecek' s procedure, but it is understood that, with this type of alkali equilibration, the key
`
`parameter is the number of exchanges rather than the total exchange time. The resulting powder
`
`was washed thoroughly with distilled deionized water.
`
`9. The powder from the NaCl treatment was subjected to two Cu acetate treatments, under the
`
`same conditions described in Dedecek et al., Table 2, entry on row 11. The final product was
`
`washed thoroughly with distilled deionized water. Elemental analysis revealed 58.47% Si02,
`
`22.16% Ah03 , 11.4% CuO, 5.17% K20, 2.57% Na20. Based on these data, the Cu/Al ratio was
`
`0.33.
`
`NOx Conversion Testing:
`
`10. The natural and synthetic samples made in accordance with paragraph 5-9 above were tested
`
`for fresh and aged NOx conversion. Each catalyst sample was disposed on a 1 inch diameter X 3
`
`inch long cellular ceramic core having a cell density of 400 cells per square inch and a wall thickness
`of 6 mil at a catalyst loading that was in the range of 2.28 and 2.52 g/in3
`
`. They were then tested for
`
`nitrogen oxides selective catalytic reduction efficiency and selectivity by adding a feed gas mixture
`
`of 500 ppm of NO, 500 ppm of NH3 , 10% 0 2, 5% H20, balanced with N2 to a steady state reactor
`containing the catalyst core at a space velocity of 80,000 hr- 1 across a 150 °C to 460 °C temperature
`
`range.
`
`11. The samples were then hydrothermally aged at 850 °C for six hours. The samples were then
`
`each tested again for NOx conversion using the same parameters as for fresh. A plot of the fresh and
`
`3
`
`Exhibit 2011.003
`
`

`
`Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`aged conversion is shown below for the natural chabazite:
`
`100 -----------------------------------------------------------------------------------------------------------------------------------------------------,
`/
`-------
`I
`
`90+--~~~~~~~~~~---=-~-------~~~~~
`
`80+--------------------~--------1
`
`~ 60 - r - - - - - - - - - - - - - - - - - - - - - - - - - - - - j
`0
`'iii
`~ 50 - r - - - - - - - - - - - - - - - - - - - - - - - - - - - - j
`g
`• 1-- Natural Chabazite, fresh I
`5 40 H-a- Natural Chabazite, aged c - - - - - - - - - - - - - - - - - - - - - j
`z
`
`100
`
`150
`
`200
`
`350
`300
`250
`Temperature (Deg C)
`
`400
`
`450
`
`500
`
`12. As shown in the plot, after aging, the NOx conversion of the natural chabazite was destroyed
`
`across the entire temperature range. This material would not be a material of interest as an ammonia
`
`SCR catalyst, as the fresh conversion is useless if the catalyst can not survive hydrothermal aging
`
`and maintain high conversion over a temperature range of 200 to 450 °C. The excellent fresh and
`
`aged performance of the catalyst claimed in the '662 patent is quite unexpected in comparison to
`
`these results.
`
`4
`
`Exhibit 2011.004
`
`

`
`Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`13. A plot of the fresh and aged conversion of the synthetic sample prepared according to
`
`paragraphs 7-9 is shown below:
`
`100 .................................................................................................................................................. .
`
`75~-~~~~~~~~~~~~----1---=-~s~yn~th-e~tic~C~h~ab-az~it-e,~fre-s~h
`-a- Synthetic Chabazite, aged
`
`100
`
`150
`
`200
`
`350
`300
`250
`Temperature (Deg C)
`
`400
`
`450
`
`500
`
`14. This material showed extremely poor fresh and aged conversion. Aging destroyed the NOx
`
`conversion of the material. It should be noted that both the fresh and aged samples show negative
`
`NOx conversion at approximately 450°C. Instead of converting NOx to nitrogen, these samples
`
`produce NOx at these temperatures. This would not be a material of interest as an ammonia SCR
`
`catalyst. The excellent fresh and aged performance of the catalyst claimed in the '662 patent is quite
`
`unexpected in comparison to these results.
`
`Zones Example 1
`
`15. I have reviewed the Zones reference, which discloses only one working example. Examples
`
`1-4 show synthesis of a SSZ-62 sample which was then calcined and underwent NH4 exchange, and
`
`ultimately to the proton form, H+ -CHA with a silica to alumina ratio of 22.
`
`16. I located data for an H+-CHA sample that was tested for NOx conversion using ammonia
`
`SCR. The testing was performed by disposing the catalyst on a 1 inch diameter X 3 inch long
`
`cellular ceramic core having a cell density of 400 cells per square inch and a wall thickness of 6 mil
`at a catalyst loading of 2.13 g/in3
`
`.
`
`17. The sample was tested for nitrogen oxides selective catalytic reduction efficiency and
`
`selectivity by adding a feed gas mixture of 500 ppm of NO, 500 ppm of NH3 , 10% 0 2, 5% H20,
`
`balanced with N2 to a steady state reactor containing the catalyst core at a space velocity of 80,000
`
`5
`
`Exhibit 2011.005
`
`

`
`hr- 1 across a 190 °C to 600 °C temperature range. A plot of the NOx (solid line) and NH3 (dashed
`line) conversion is shown below:
`
`Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`100
`
`90
`
`80
`
`70
`
`60
`
`~
`9.......
`> 50
`c
`0
`0
`
`40
`
`30
`
`20
`
`10
`
`0
`1 00
`
`I-NO Conv. [%]
`1- NH3 Conv. [%]
`
`I
`
`/ / /
`
`//
`/y
`
`---=----- ....- -
`- ~
`
`1 50
`
`200
`
`250
`
`300
`
`350
`
`400
`
`450
`
`500
`
`550
`
`600
`
`temperature [ 0C]
`
`18. The catalyst exhibited essentially no fresh NOx conversion until about 475 °C. As the
`
`catalyst exhibited no fresh NOx conversion in the temperature range of interest, the sample was not
`
`aged and tested, as doing so would be pointless. The excellent fresh and aged performance of the
`
`catalyst claimed in the '662 patent is quite unexpected in comparison to these results.
`
`Yuen Example 3
`
`19. The sample prepared in accordance with the Zones reference would also be representative of
`
`Example 3 in Yuen and a suitable indirect comparison of Example 3 of Yuen. In fact, conversion of
`
`the H+ form in the Yuen example would be expected to perform worse than Zones, because the silica
`
`to alumina ratio in Yuen is very high, and at a silica to alumina ratio of 166 versus 30 for the sample
`
`tested, lower NOx conversion would be expected.
`
`Hydrocarbon SCR Testing
`
`20. I was asked to provide data pertaining to hydrocarbon SCR for Cu-SAP0-34 and/or Cu-SSZ-
`
`13 samples. One of my colleagues provided data from a separate research program for HC SCR for
`
`6
`
`Exhibit 2011.006
`
`

`
`Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`hydrocarbon SCR using Cu-SAP0-34 for pellet samples run in a microreactor at a space velocity of
`40,000-50,000 hr- 1
`
`It has been my experience that use of hydrocarbon SCR data on a material is
`
`.
`
`irrelevant to predict ammonia SCR behavior on the same material. Different hydrocarbon reductants
`
`behave differently on the same material. The Halasz article, attached as Exhibit C-4 to Dr. Lercher' s
`
`declaration, is irrelevant to the '662 invention because there is no hydrothermal aging data. It is an
`
`overgeneralization to conclude from Halasz that if a catalyst worked with one reductant, it would
`
`work with a different reductant. Halasz only tests ammonia at 573 K, which is above the low
`
`temperature region of interest in the '662 patent. Propane and propene had significantly different
`
`performance as reductants over the same catalyst. Three sample runs were performed using
`
`propylene reductant, a simulated gasoline exhaust gas reductant (containing 41.3 % isooctane; 38 %
`
`m-xylene; 11.4% 1-octene; 9.3% n-octane) and a simulated diesel exhaust gas reductant (containing
`
`37.8% m-xylene; and 62.2% n-octane). Propylene reductant is only of academic interest because
`
`hydrocarbon SCR is viewed as an attractive option when a hydrocarbon gas on-board the vehicle can
`
`be used as a reductant. Propylene would require an additional reservoir and injector. Thus, samples
`
`tested with the simulated diesel and gasoline exhaust are of much greater interest as real world
`
`examples of reductants. Samples were tested as fresh and aged at temperatures of 700 °C and 800
`
`°C for different Cu-SAP0-34 samples, as compared to Cu-ZSM-5. The best results for a Cu-SAP0-
`
`34 sample, with 4.37% CuO, appear in paragraphs 21-23. For these data, the negative conversion
`
`values shown are simply an artifact of the very low NOx conversions, which are calculated from
`
`inlet and outlet NOx values.
`
`21. For propylene, the conversions were as follows:
`
`200 °CFresh
`
`400 °C Fresh
`
`Cu-ZSM-5
`
`Cu-SAP0-34
`
`-7.4%
`
`5.9%
`
`39.8%
`
`3.2%
`
`22. For simulated gasoline, the conversions were as follows:
`
`200 °CFresh
`
`400 °C Fresh
`
`Cu-ZSM-5
`
`Cu-SAP0-34
`
`-0.8%
`
`6.2%
`
`32.9%
`
`-1.9%
`
`23. For simulated diesel, the conversions were as follows:
`
`200 °CFresh
`
`400 °C Fresh
`
`Cu-ZSM-5
`
`-2.9%
`
`40.5
`
`7
`
`Exhibit 2011.007
`
`

`
`Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`Cu-SAP0-34
`
`0.4%
`
`-1.5
`
`24. For the aged samples, the performance for SAP0-34 was worse for simulated gasoline and
`
`diesel, with the exception of one sample that had 2% conversion at 400 °C for simulated gasoline.
`
`The catalytic activity in terms of NOx conversions for Cu-SAP0-34 using simulated gasoline and
`
`diesel reductants was so poor, these materials were not pursued as commercial catalysts.
`
`Further Examples in Accordance with the '662 patent
`
`25. I was asked to provide additional Examples representative of the '662 invention. I obtained
`
`the following data from a colleague, from a study pertaining to various silica to alumina mole ratio
`
`aluminosilicate zeolites and containing varying ratios of Cu/ Al. The samples were prepared
`
`similarly to the Examples in the '662 patent All zeolites samples were calcined and ammonium
`
`exchanged to reduce Na content to levels typically lower than 0.01 wt% Na20. The ammonium
`
`form was then copper exchanged in an aqueous solution of copper acetate to provide the reported
`
`compositions. Samples were prepared into pellets 0.5 to 1 mm long by 2 mm in diameter. Samples
`were aged in 10% H20, 10% 0 2, balance N2 at a space velocity of 12,500 h- 1 for 6 hours at 850 ° C.
`
`This study involved only hydrothermally aged NOx conversion, which is the parameter of interest to
`
`BASF's customers. An inlet gas mixture was formed containing 500 ppm NO, 500 ppm NH3 , 10%
`0 2, 5 % H20 and balance He at a space velocity of 80,000 h- 1
`200 °C and 450 °C.
`
`. NOx conversion was measured at
`
`Silica/ Alumina
`
`Cu/Al Aged NOx conversion 200 °C
`
`450 °C
`
`Sample 1 14.4
`
`Sample 2 18.2
`
`Sample 3 24.2
`
`Sample 4 49.2
`
`0.24
`
`0.25
`
`0.27
`
`0.32
`
`9%
`
`68%
`
`70%
`
`56%
`
`57%
`
`75%
`
`80%
`
`63%
`
`The data above shows that at just below the claimed silica to alumina ratio, aged NOx conversion at
`
`200 °C was unacceptably low. For the sample 2, the aged conversion improved. Sample 4 showed
`
`lower conversion than samples 2 and 3. Additional experiments with varying Cu/Al ratio and
`
`exchange conditions was not conducted, but Sample 4 could be optimized with further
`
`experimentation.
`
`8
`
`Exhibit 2011.008
`
`

`
`Inter Partes Reexamination No. 95/001,453
`Second Declaration of Ahmad Moini, Ph.D.
`
`I hereby declare that all statements made herein of my own knowledge are true and that all
`
`statements made herein on information and belief are believed to be true; and further that these
`
`statements were made with the knowledge that willful false statements and the like so made are
`
`punishable by fine or imprisonment, or both, under Section 1001 of Title 18 of the United States
`
`Code, and that such willful false statements may jeopardize the validity of the above-identified
`
`patent.
`
`Dated: December 18, 2011
`
`By:
`
`Ahmad Moini, Ph.D.
`
`Respectfully submitted,
`
`9
`
`Exhibit 2011.009

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