Progress In Managing PFCs
-- Semiconductor International, 11/1/1998
Perfluorocarbon emission
reduction approaches take many forms including abatement, capture, recycle, use
of alternative chemistries and process optimization. At SEMI's PFC Technical
Update in July, parties reported on refined methods of abatement as well as
process optimization to obtain short-term reductions in PFC emissions until
suitable alternatives can be identified.
The PFCs most commonly used in semiconductor processing along with their global warming potentials (GWPs) are shown in Table 1. Non-PFCs such as NF3 and CHF3 are included in the list due to their high GWP, indicating the relative effect on the environment relative to carbon dioxide. CF4, C2F6, C3F8 and NF3 gases are treated in a fixed bed catalytic reactor. Roy Brown and Joseph Rossin of Guild Associates (Dublin, Ohio), reported greater than 95% destruction of the three PFCs at operating temperatures between 600-700°C, with byproducts of CO2 and HF. Unlike PFCs, NF3 is completely destroyed at low temperatures, resulting in the near-stoichiometric formation of NOx. NOx, both an acid rain precursor and contributor to urban smog, can be reduced using ammonia, yet does not sufficiently reduce NOx levels. Work in this area is continuing.
| Table 1. PFC Characteristics | |||||
| Chemical name | Formula | Toxicity | Lifetime (years) | Global warmng potential (100 years) |
Processes |
| Carbon dioxide | CO2 | n/a | 50-200 | 1 | - |
| HC-23 | CHF3 | low | 250 | 12,100 | Oxide/nitride etch |
| Nitrogen trifluoride | NF3 | medium-high | 740 | 6300-13,100 | Oxide/nitride etch, oxide/nitride chamber cleans |
| HC-218 | C3F8 | low | 2600 | 7000 | Oxide/nitride chamber cleans |
| Sulfur hexa-fluoride | SF6 | low | 3200 | 24,900 | Oxide/nitride etch, oxide/nitride chamber cleans |
| HC-14 | CF4 | low | 50,000 | 6300 | Oxide/nitride etch, oxide/nitride chamber cleans |
| HC-116 | C2F6 | low | 10,000 | 12,500 | Oxide/nitride chamber cleans |
Because the catalyst is readily deactivated by SiF4, it must be scrubbed prior to entering the catalyst bed. NF3 is the most readily destroyed compound, followed by CHF3. The three PFCs require processing at 200°C to obtain comparable reductions. Over the course of the test, almost 3.5 kg of C2F6 was destroyed using a small amount of catalyst according to a catalyzed hydrolysis mechanism.
Tool optimization is commonly used to reduce PFC emissions, yet often results in the generation of increased volumes of hazardous air pollutants such as fluorine gas (F2), silicon tetrafluoride (SiF4), and to a lesser extent, HF and carbonyl fluoride (COF2). The generation of such pollutants shifts the focus to efficient abatement of byproducts. With the concomitant goal of minimizing the use of resources, Josep Arno of ATMI-EcoSys Corp. (Danbury, Conn.) evaluated abatement efficiency of a point-of-use water scrubber at removing F2 and SiF4 while inhibiting the generation of oxygen difluoride (OF2). Hydrolysis of F2 produces HF, O2 and H2O2, with small amounts of OF2. Hydrolysis of SiF4 produces SiO2 and aqueous HF. Arno found that a standard water scrubber equipped with a polishing counter-current packed-bed installation at the scrubber exhaust improved F2 removal efficiency by 60%.
Using effluent with SiF4 gas concentrations exceeding those normally released during plasma chamber cleans, outlet concentrations of HF and SiF4 were slightly above the detection limit of the FTIR spectrometer and significantly below their threshold values of 1 ppm for SiF4 and 3 ppm for HF. For high inlet concentrations of F2, a proprietary abatement enhancing chemical was injected to discourage the formation of OF2, while decreasing HF and F2 outlet concentrations by a factor of 10. Caustic injection (of NaOH), while it does enhance fluorine abatement, generates unacceptable levels of OF2. Arno found that under all conditions tested, the water scrubber removed over 99% of fluorine delivered, with no compromise in scrubber integrity. Hazardous air pollutants emission levels are expected to increase by a factor of 1.5-3.3 upon transition to 300 mm wafers.
Michael Daniels, Albert Cheng and Janice Chen of Texas Instruments (Dallas
Texas) tested C3F8 as a drop-in replacement for
C2F6 for cleaning Applied Materials' Centura dielectric
CVD 5200 chambers. As shown in previous studies (see 'Reducing PFC Emissions
Using C3F8-Based PECVD Clean,' Semiconductor
International, Feb. 1998, p.85), C3F8 can offer
improved gas utilization in the chamber cleaning process, a 47% decrease in
consumable costs and a 64% decrease in PFC emissions, while showing no
statistical differences in die yield, device parameters and reliability
performance. In this study, a Novellus Concept Two Sequel PECVD tool was used.
In the TI study, C3F8: provides identical or shorter
cleaning times, reduces consumable costs by 23%, reduces PFC emissions by 52%,
reduces CF4 emission levels and shows no difference in film
properties.