WikiPrint - from Polar Technologies

Ecosim uses a very simple strategy to represent nutrient cycling and potential nutrient limitation of primary production rates. It is assumed that at any instant in time the system has a total nutrient concentration *N _{T}*, which is partitioned between nutrient 'bound' in biomass versus free in the environment (accessible to plants for nutrient uptake). That is,

Changes in nutrient loading can be simulated by assigning a time forcing function number to *N*_{T} on the Ecosim parameters form, in which case N_{T} is calculated as N_{T} = ft *N*_{To} where *N*_{To} is the Ecopath base estimate of N_{T} (at the start of each simulation) and ft is a time multiplier (*f*_{t}* * = 1 implies Ecopath base value of *N*_{T}) supplied by the user the same as any other time forcing function. Note that under the moving equilibrium assumption, changes in *f _{t}* can be viewed as caused by either changes in input rate

The Ecopath base estimate *N*_{T}*o*_{'} of total nutrient is entered by specifying the base free nutrient proportion *pf = Nf / N*_{T}*o*_{'} on entry to Ecosim (also on the Ecosim parameters form: *Time dynamic (Ecosim) >Input > Ecosim parameters*), from which the Ecosim initialization can calculate N_{T}o_{} as simply *N*_{To}* = ?i ?i Bi / (1-pf)*. Note here that the units of nutrient concentration are contained in the per-biomass relative nutrient concentrations *? _{i}*, and these need not be specified in any particular absolute units. During each simulation,

Primary production rates for producer pools *j* are linked to free nutrient concentration during each simulation through assumed Michaelis-Menten uptake relationships of the form *P/B*_{j}*=P/B*_{max,j}* N*_{f}*/(K*_{j}*+N*_{f}*)*, where the parameters *P/B*_{max,j} and *K*_{j} are calculated as part of the Ecosim initialization using input estimates by the user of the ratios *P/B _{max,j} / P/B*

The default free nutrient proportion pf is set at unity, which causes *N*_{f} to be virtually constant over time (and hence *P/B*_{j}'s to be virtually independent of nutrient concentration changes). Thus to ?turn on? nutrient limitation effects, you must set a lower value for pf, (e.g., 0.3) on the Ecosim parameters form.

Users should be aware that this simple approach to accounting for nutrient limitation can interact with the numerical method used to simulate very fast phytoplankton dynamics over time, to cause numerical instability or ?chattering? in the values of phytoplankton biomass. This happens mainly in cases where *p*_{f} is low, so that *N*_{f}is initially small. Then any biomass decline in the system (e.g. due to decline in zooplankton biomass) results in a relatively large increase in *N*_{f}, which can cause an over-response in the calculated phytoplankton biomass(es) *B*_{j}, which then drives* N*_{f} to near zero, which in turn causes too large a decrease in calculated *B*_{j} for the next monthly Ecosim time step.

Chattering can be reduced by using the Runge-Kutta integration option and/or higher pf settings. Improved numerical integration procedures should allow us to avoid the problem entirely in future Ecosim versions, but at present the computational cost of avoiding the problem by 'brute force' (shorter simulation time steps) would be prohibitively expensive of computer time.

Note further that the single free nutrient concentration *N*_{f}'is linked to all primary producer groups in the model (through the uptake kinetics-P/B relationships), implying competition among all plant types in the model for free nutrients. This can cause major shifts in primary production structure over time, e.g. between benthic and pelagic primary production and between grazeable and non-grazeable algal types.