Ba. Kelly-gerreyn et al., Calibration of an early diagenesis model for high nitrate, low reactive sediments in a temperate latitude estuary (Great Ouse, UK), MAR ECOL-PR, 177, 1999, pp. 37-50
The description and calibration of a reaction-diffusion model of early diag
enesis are presented. Unlike previous models it has been developed for a te
mperate latitude estuary (Gt Ouse, UK) impacted by high nitrate concentrati
ons (annual mean 700 mu M). Five variables, O-2, NO3-, NH4+, SO42- and S2-
are modelled from the steady state distributions of bulk total organic carb
on (TOC) (i.e, a l-G model). Three methods for deriving the first order rat
e constant, k, for TOC mineralisation are tested: (1) data calculated k val
ues [i.e. (depth integrated total mineralisation rate) divided by (depth in
tegrated TOC inventory)]; (2) an exponential formulation. k(z) = k(0) e(-al
pha z) (k(0) = k at sediment surface, alpha = reactivity coefficient of dec
rease, z = depth); and (3) use of separate k values for individual minerali
sation pathways. Method a underestimates observed fluxes of solutes across
the sediment-water interface (SWI) by up to an order of magnitude. This is
due to an inappropriate use of the calculated kin the model. The calculatio
n of k yields an overall net Value which implicitly accounts for all factor
s acting on mineralisation. Such factors (e.g. oxidant Limitation of organi
c decay) are explicitly modelled. Consequently, k is significantly reduced
by factors applied to it in the model which have previously been accounted
for in the calculation. In Method 2, measured NO3- fluxes are overestimated
by up to a factor of 7. To reproduce measured benthic oxygen demands and s
ulphate reduction rates, a cannot be simultaneously fitted to the NO3- flux
es. The high overlying NO3- concentrations result in model denitrification
that cannot reproduce the degree of Limitation that actually occurs. Method
3 reproduces the data (i.e. both stoichiometrically derived mineralisation
rates and measured solute fluxes at the SWI) to a high degree (r > 0.99, p
< 0.001), but at the expense of increasing the degrees of freedom in the m
odel and conceptual simplicity. These results cast doubt over the universal
applicability of diagenetic models for estuarine systems exposed to high N
O3- concentrations. It is concluded that the use of commonly calculated fir
st order rate constants (Method 1) and the frequently used exponential func
tion (Method 2) in diagenetic models cannot be relied upon to reproduce obs
ervations in high NO3- estuaries. Previous stoichiometric calculations sugg
ested that all of the measured ammonium fluxes across the SWI in the Ct Ous
e could be accounted for with oxygen, nitrate and sulphate reduction alone.
With these latter processes the model (Method 3) underestimates the observ
ed ammonium fluxes by up to 44 % at 3 out of 4 sites. This suggests that ot
her mineralisation pathways (e.g, nitrate ammonification) are active in the
Great Ouse sediments.