What the
Written Record Tells Us
(OK, this is
an academic literature review)
Alabama’s forest products industry
is dominated by large corporations whose ownership of forest land and mills plays
a major role in Alabama’s rural economy (Bliss and Meuhlenfeld 1991).
In 1999, manufacturing in the forest products sector of Alabama
accounted for $4.3 billion in value-added, $10.7 billion in value of shipments,
$1.5 billion in payroll, and 41,500 jobs (U.S. Census Bureau 1999). Pulpwood production and the manufacturing of
pulp and paper products represents the largest segment
of this sector. The South produces 77%
of the nation’s pulpwood (USDA Forest Service n.d.),
and Alabama is the nation’s leading state in pulpwood
production (Johnson and Steppleton 1999).
Pulp and paper production is a
capital-intensive operation, with individual mills representing up to $2
billion in investment (Bailey et at. 1996a). There are at present 14 large pulp and paper
mills operating in Alabama. Workers at these mills are among the best
paid in Alabama’s rural economy, but their numbers are shrinking as mills close
(two closed within the past five years) and as new technologies come on line
which replace labor (Bailey et al. 1996b; Lupo in
prep.). The rural development impact of
these positive contributions have been muted by extraordinarily low property
taxes on forest land throughout Alabama (PARCA 2001), and tax abatements which
have made it possible for pulp and paper mills annually to escape millions of
dollars in property taxes (Joshi 1997; Joshi et al. 2000).
In recent years, the combined
effects of corporate consolidation and technological change have led to
increasing economic concentration in the forest products sector (Sinclair,
Bailey, and Dubois in press). The
introduction of mechanized whole tree harvesting operations has led to the
virtual demise of labor-intensive shortwood pulpwood
producers, once a significant source of employment for the rural workforce
(Bliss and Flick 1994). Operating shortwood pulpwood producers allowed for an expanded menu
of forest management alternatives for forest owners. In 1979, 78% of southern pulpwood loggers
produced shortwood.
Only fifteen years later that figure had dropped to 20% (Munn et al.
1998). Similarly, smaller sawmills which
once dotted the landscape of rural Alabama have closed down as
economies of scale resulted in fewer but larger mills dominating the
industry. The decline in the
availability of shortwood pulpwood producers directly
led to a decline in forest management alternatives, marginalizing many forest
owners out of the timber marketplace (Toms et al. 2001).
The process of economic
concentration has included ownership in forestland. In contrast to national trends towards
fragmentation, in Alabama small forest land tracts
are being consolidated into larger holdings (Bliss, Sisock
and Birch 1998; Sisock 1998). More than half (58%) of Alabama’s forest land is owned by
1% of all ownership units, and this concentration is most marked in the Black
Belt region (Bliss, Sisock and Birch 1998). Data from the 1980s indicate
African-Americans in Alabama own only 4% of the private
forest acreage (Rosson and Doolittle 1987). Research on the decline in African-American
farm ownership in Alabama (Zabawa,
Siaway, and Baharanyi 1990;
Zabawa 1995), and on-going research on problems faced
by minority forest land owners (Crim in prep.; Crim, Dubois and Bailey in prep.) suggest that conditions
have not improved since then. The
process of consolidation into ever larger tracts could continue (Bailey,
Sinclair, and Dubois in prep.) if current research on genetic engineering were
to yield dramatic increases in productivity promised by some proponents (Sedjo 1999).
The net result of these changes is
that the connection between rural community and the forested landscape in Alabama has weakened. Forest land owners who have sufficient
acreage to produce timber on a commercial basis have done well, as have those
fortunate enough to be employed in mechanized logging operations, in the
remaining saw mills, or in the large pulp and paper mills. However, during the period 1950-2000, when
economic conditions in rural Alabama generally improved,
non-metropolitan timber-dependent counties lagged behind both metro and
non-metro counties which were not timber dependent (Bliss et al. 1993;
Robinson, Howze and Norton in press). This finding also holds true for non-metro
counties hosting large pulp and paper mills (Bliss and Bailey in press; see
Appendix 2).
The forest products industry of Alabama is most heavily
concentrated in the state’s timber dependent Black Belt counties, where
problems associated with poverty and unemployment are most severe (Walkingstick 1996; Bliss, Walkingstick,
and Bailey 1998). Northrup
(1970) documented discriminatory labor practices that effectively excluded
African-Americans from good jobs in the paper industry. Bailey et al. (1996b) reported that racial
discrimination in Alabama has not been entirely
eradicated in this industry. This is
significant because poverty in this region is most concentrated in minority
households (U.S. Census Bureau 2000).
The connection between natural
resources and persistent rural poverty is not limited to Alabama (RSS 1993). One of the most common causes of this
connection is the lack of local control over resources and the economy (Bailey
et al. 1993; Peluso et al. 1994). The concentration of economic power in
relatively few hands, and the absence of local hands holding this power, leaves
local communities powerless to deal with decisions made far away (RSS
1993). This in turn undermines the
ability of local communities to promote development. Norton (2001) found that social capital
(trust and civic mindedness) was strongest in those Alabama Black Belt counties
where the economy was relatively diverse and weakest where it was not.
Even though most of the forest land of Alabama’s Black Belt is in large
ownership units, there are a large number of owners of small tracts who have
limited opportunity to market timber from their land. This is the population of landowners we wish
to study
The average forest size of the non-industrial
private owner is declining. Greene et
al. (1997) documented a trend towards decreasing timber stand and timber sale
size in Georgia and noted the need for technology to better address the harvesting and silvicultural needs of smaller forest ownerships. Given existing harvesting and silvicultural management paradigms, some forest
practitioners and forest policy analysts bemoan declining forest ownership size
as a "small-owner problem."
Others view small-forested tracts as an opportunity to develop
sustainable, small-scale harvesting that can operate efficiently, and protect
the amenity values demanded by society while meeting the diverse management
objectives of non-industrial private forest (NIPF) owners. DeCoster (1998) in
an analysis of NIPF ownership fragmentation stated, “We need new approaches and
technologies designed for small [forested] parcels.”
Small-scale harvesting systems, such as farm
tractor-based systems, may complement large-scale mechanized logging by filling
the harvesting niches of small forested tracts, low sawlog
volume harvests, and aesthetically sensitive areas. For example, use of animals (horses and
mules) to haul logs out of the woods is an alternative available in some
locations. There are those in the
forestry community that question the practicality of using animals in logging
operations, claiming any interest in animals is just nostalgic wishfulness.
However, results of a survey of natural resource managers in the
northeast U.S. found that 58% agreed with
the statement: “If there were loggers who used animals in my area, I would use
animal logging over conventional methods in some situations” (Egan 1998). Toms et al. (2001) estimated there were 50
active animal logging operations in Alabama in 1998.
Small forested tracts are not well
served by contemporary logging operations.
The challenge is to identify and develop small-scale harvesting systems
that can operate efficiently while meeting the diverse management objectives of
non-industrial private forest (NIPF) landowners (DeCoster
1998). A 1991 survey of NIPF owners in Alabama indicated 71% considered
income from timber sales an important benefit of forest ownership. However, only 25% indicated this was the
primary management objective (Bliss 1993).
Almost 60% reported that non-commodity values (e.g., maintaining family
ownership, protecting wildlife, and personal recreation) were the primary
benefits of ownership. Poitras (n.d.) found that 43% of
NIPF owners would not allow heavy equipment to harvest timber on their land
because of adverse forest impacts (e.g., soil compaction, soil erosion,
incompatibility with selective harvesting).
In contrast, 45%
of respondents were willing to accept less money for their timber if low impact
logging (e.g., animal logging, tractor logging) were used to improve their
forest’s future health and productivity.
The effect of tract size on
harvesting costs has been examined. Cubbage (1983) reported that harvest costs for
capital-intensive, highly mechanized systems are more sensitive to tract size
than low-capital, labor intensive shortwood harvesting
systems. Highly mechanized systems have
higher move costs, meaning that it is inefficient for such operations to stop
and harvest small tracts. Cubbage (1983) reported
that shortwood harvesting operations had the lowest
harvesting cost for tracts less than 20 acres.
Toms et al. (2001) reported that 20 acres represents the median tract
size for animal logging operations in Alabama, and that in this range
such low capital harvesting systems may be cost effective. DeCoster (2000)
suggests that forest parcels below 50 acres often cannot be harvested through
conventional forestry approaches. From a
rural development perspective, the viability of forestry on small landholdings
raises other concerns. Minority and
limited resource landowners in Alabama generally have smaller than
average landholdings (Schelhas 2000). Gan and Kolison (1999), studying minority forest landowners in two Southeastern Alabama counties, found a median
forest land holding of 70 acres, with one-third of forest landowners having
less than 50 acres. Making an economic
return from forest lands may be critical in to small landowners
ability to retain their lands and maintain their economic well being (Zabawa et al 1990; Tufts and Zabawa
2000). But this requires greater
attention from researchers and extensionists to the
practice of forestry on small parcels.
Literature cited
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