Litter bags with natural mixed litter were incubated until approximate
to 60-70% mass loss in two oak-hornbeam and two pine-beech forest sta
nds in southern Poland. At the same stands the input of chemical eleme
nts with throughfall was followed. Decomposition constants k for the o
ak-hornbeam litters were -0.57 and -0.55, and for the pine-beech litte
rs -0.30 and -0.27. Chemical elements (except for Cu and Mn) revealed
similar relative mobility in the four litters. On average the elements
could be ordered by decreasing mobility as follows: K > Mg > Ca > S >
Cu > Na > Mn = N > Cd > Pb = Zn > Fe. Instead of the two presupposed
factors controlling litter decomposition, biological and chemical, thr
ee factors were specified: (1) biological, dominating the decay of org
anic matter and the dynamics of N, Ca, Mg, Mn, and S; (2) physical, do
minated by leaching and atmospheric deposition, and controlling the dy
namics of organic matter, K, Na, Pb, Cd, and Zn; and (3) chemical, det
ermining the dynamics of Fe, Zn, Pb, and Cd through the fixation of me
tal ions to humic substances. Potassium was the only element that decr
eased in concentration in all litters, while the concentrations of N,
Na, Fe, Zn, Pb, and Cd increased in all litters. S, Ca, Mg, and Mn con
centrations revealed different patterns in different litters, presumab
ly due to the differences in initial concentrations and soil acidity.
No clear trend was found for Cu. In all litter types, Fe, Zn, Pb, and
Cd significantly increased in absolute amounts at the end of litter-ba
g incubation. In all four stands the input with throughfall was high e
nough to explain the increases in amount of elements, with the excepti
on of Fe in the oak-hornbeam litters.