Managerial Challenge
In the second
decade of the twenty-first century, companies all across the industrial
landscape are seeking to achieve sustainability. Sustainability is a powerful
metaphor but an elusive goal. It means much more than aligning oneself with
environmental sensitivity, though that commitment itself tests higher in
opinion polling of the latent preferences of American and European customers
than any other response. Sustainability also implies renewability and longevity
of business plans that are adaptable to changing circumstances without
uprooting the organizational strategy. But what exactly should management
pursue as a set of objectives to achieve this goal?
Management
response to pollution abatement illustrates one type of sustainability
challenge. At the insistence of the Prime Minister of Canada during the Reagan
Administration, the U.S. Congress wrote a bipartisan cap-and-trade bill to
address smokestack emissions. Sulfur dioxide and nitrous oxide (SOX and NOX)
emissions precipitate out as acid rain, mist, and ice, imposing damage
downwind over hundreds of miles to painted and stone surfaces, trees, and
asthmatics. The Clean Air Act (CAA) of 1990, amended in 1997 and 2003, granted
tradable pollution allowance assets (TPAs) to known polluters. The CAA also
authorized an auction market for these TP A assets. The EPA Web site (www.epa.gov) displays on a daily basis the
equilibrium, market-clearing price (e.g., $250 per ton of soot) for the use of
what had previously been an unpriced common property resource—namely, acid-free
air and rainwater. Thereby, large point-source polluters like power plants and
steel mills earned an actual cost per ton for the SOX and NOX-laden soot
by-products of burning lots of high sulfur coal. These amounts were prompdy
placed in spreadsheets designed to find ways of minimizing operating costs.2
No less importantly, each polluter felt powerful incremental incentives to
mitigate compliance cost by reducing pollution. And an entire industry devoted
to developing pollution abatement technology sprang up.
The
TPAs granted were set at approximately 80 percent of the known pollution taking
place at each plant in 1990. For example, Duke Power's Belews Creek power plant
in northwestern North Carolina, generating 82,076 tons of sulfur dioxide acidic
soot annually from burning 400 train carloads of coal per day, was granted
62,930 tons of allowances (see Figure 1.1 displaying the 329 x 365 = 120,085
tons of nitrous oxide). Although this approach "grandfathered" a
substantial amount of pollution, the gradualism of the 1990 cap-and-trade bill
was pivotally important to its widespread success. Industries like steel and
electric power were given five years of transition to comply with the regulated
emissions requirements, and then in 1997, the initial allowances were cut in
half. Duke Power initially bought 19,146 allowances for Belews Creek at prices
ranging from $131 to $480 per ton and then in 2003 built two 30-story
smokestack scrubbers that reduced the NOX emissions by 75 percent.
Another major electric utility,
Southern Company, analyzed three compliance choices on a least-cost cash flow
basis: (1) buying allowances, (2) installing smokestack scrubbers, or (3)
adopting fuel switching technology to burn higher-priced low-sulfur coal or
even cleaner natural gas. In a widely studied case, the Southern Company's
Bowen plant in North Georgia necessitated a $657 million scrubber that after
depreciation and offsetting excess allowance revenue was found to cost $476
million. Alternatively, continuing to burn high-sulfur coal from the
Appalachian Mountain region and buying the requisite allowances was projected
to cost $266 million.
And finally, switching to low-sulfur coal and adopting fuel switching
technology was found to cost $176 million. All these analyses were performed on
a present value basis with cost projections over 25 years.
Southern
Company's decision to switch to low-sulfur coal was hailed far and wide as
environmentally sensitive. Today, such decisions are routinely described as a
sustainability initiative. Many electric utilities support these sustainable
outcomes of cap-and-trade policies and even seek 15 percent of their power from
renewable energy (RE). In a Case Study at the end of the chapter, we analyze
several wind power RE alternatives to burning cheap high-sulfur large carbon
footprint coal.
The
choice of fuel-switching technology to abate smokestack emissions was a
shareholder value-maximizing choice for Southern Company for two reasons. First,
switching to low-sulfur coal minimized projected cash flow compliance costs
but, in addition, the fuel-switching technology created a strategic flexibility
(a "real option") that created
additional shareholder value for the Southern Company. In this chapter, we will
see what maximizing capitalized value of equity (shareholder value) is and what
it is not.
Discussion Questions
- What's the basic externality problem with acid rain? What objectives should management serve in responding to the acid rain problem?
- How does the Clean Air Act's cap-and-trade approach to air pollution affect the Southern Company's analysis of the previously unpriced common property air and water resources damaged by smokestack emissions?
- How should management comply with the Clean Air Act, or should the Southern Company just pay the EPA's fines? Why? How would you decide?
- Which among Southern Company's three alternatives for compliance offered the most strategic flexibility? Explain.
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