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Fig. 2.10 Long-run trends in real prices of rewood, coal and oil in Italy (1700
-
1985 in 1911 ITL
per TOE). Source Malanima ( 2006 , pp. 70
-
71)
forest, maquis, etc.). 110 In his overview on world-wide deforestation Michael
Williams suggests that, in Europe, before the coming of the fossil fuel era, timber
and
rewood shortages were more of a local or regional feature than a general one,
and he discards charcoal consumption in industrial uses as a relevant factor. 111 On
the opposite side, Paolo Malanima bears no doubts when he states that
from the
mid-eighteenth century onward, while Europe
s population was growing faster,
energy availability was decreasing. The result was a sharp per capita decline in
energy consumption
'
. 112 This included both food intake and fuel wood availability,
which seems to
t well with the anthropometric height decrease of Europeans
born between 1770 and 1820.
The decline of forest is borne out
according to
Malanima
rewood, which was usually faster than
the overall growth of agricultural prices. In Western European cities, between 1700
and 1800,
by the quick rise of the price of
. 113 The long-term
rewood prices increased by more than three times
evolution in Italian prices of
rewood, compared with prices of coal and oil, clearly
economic growth theory proposed by Bob Ayres and
Benjamin Warr (Fig. 2.10 ; see also Fig. 2.2 ):
In a nuanced and detailed overview of the wood shortage debate in pre-industrial
Europe, Paul Warde assesses that
ts with the
'
exergetic
'
if the European population in 1500was around half
that in 1800, and if there were general scarcities in 1500, survival could only have
been possible in 1800 as a consequence either of a radical alteration in the domestic
fuel economy, or a greatly increased woodland area or productivity. As there is very
little evidence for any of these things we must be suspicious of any claims for a general
scarcity at any time before the late eighteenth century. Western Europe had a popu-
lation of around 122 millions by 1820, and if annual domestic demand is set at about
three cubic meters per hectare, a coppiced area of 407,700 km 2 would have been
required for a sustainable supply. This approximates to the area of modern Germany
and Switzerland combined, something under a
fth of western Europe (excluding
110 Grove and Rackham ( 2001 ).
111 Williams ( 2003 ).
112 Malanima ( 2006 ), pp. 101
121.
113 Malanima ( 2006 ), pp. 116 - 118.
-
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