1.                      Wet Deposition

In LOTOS-EUROS wet deposition is treated in a simplified way. As the meteorological input does not contain detailed information on clouds the in-cloud scavenging of gases and aerosols is neglected. Hence, below we describe the parameterisations for below cloud scavenging only.

1.1                   Gases

The standard method to calculate wet deposition for soluble gases is described below.

 

We define the following parameters:

 

M:        mass (μg)

Cwater:   concentration of component in water (rain), i.e. mass of component per volume of water (μg/m3)

Cgas:     concentration of component in gas phase, i.e. mass of component per volume of air (μg/m3)

t:          time (h)

Δt:        time step (h)

V:         volume (m3)

A:         horizontal area (m2)

Δz:       layer depth (m)

P:         precipitation rate (m/h)

W:        washout ratio, the ratio Cwater/Cgas .

 

Exchange of mass takes place between gas in the air and the raindrops. Conservation of mass says:

 

.                                   (1.)

 

Since the volume of water is , we can write this equation for concentrations:

 

.           (2.)

 

We now assume that the process of falling rain from upper layers and mass getting into the raindrops can be split (operator splitting) in the following way: compute the water concentration at the end of the time step in the uppermost layer, then assume that concentration to be the input concentration for the next (lower) layer. Thus proceed to lower layers. Definingthe water concentration of the layer above the current layer (which has been computed in previous stages and is assumed constant in the current layer), then the operator splitting leads to:

 

.

 

Eq. (2.) then reads:

 

.                    (3.)

 

Dividing by and letting , we get the differential equation

 

,                                                  (4.)

 

with as solution:

Defining d, the concentration change within a layer due to wet deposition:

The concentration in layer l+1 is computed by accumulation of mass caught in rain in upper layers:

Note that there is only exchange of mass to the raindrops in layer l, if the concentration in the falling raindrops is still lower than (the restriction should hold).

 

The following algorithm is used to compute wet deposition:

 

Go from upper layer to below:

            if (return_to_atmosphere[1] OR (not_return_to_atmosphere AND ))

           

 

The meteorological input for LOTOS-EUROS supplies the amount of precipitation that reaches the ground. In reality, precipitation is on average only 50% effective which means that half of the rain drops evaporate before the drops reach the ground. This effect, which redistributes tracer mass in an air column, is neglected in the current version of LOTOS-EUROS

 

 

Component

Λbc (*106)

 SO2

0.15

HNO3

0.5

NH3

0.5

H2O2

0.5

HCHO

0.05

Table 6.1. overview of below cloud scavenging coefficients for gases

 

1.2                   Aerosols

For particles the wet deposition is calculated following Scott (1979):

 

           

 

A = 5.2 m3 kg-1 s-1

P = precipitation rate [m/s]

Vrd = Fall speed of rain droplet [m/s]

E = Collection efficiency

 

 

SO4

0.1

NO3

0.1

NH4

0.1

PPM fine

0.1

PPM coarse

0.4

Table 6.2.  Collection efficiency for aerosol particles in LOTOS-EUROS

 

1.3                   Alternative scheme for below cloud scavenging of gases

 

LOTOS-EUROS also contains an alternative and simple parameterisation to describe the below scavenging of gaseous species. The scavenging of a soluble component C is given by:

 

 

Λbc = Below-cloud scavenging coefficient

P = precipitation rate [m/s]

Δz = scavenging scale depth [=1000 m]

 

The scavenging coefficients (Λbc) were adopted from EMEP (2004; website) and are listed in Table 6.3.

 

 

Component

Λbc (*106)

 SO2

0.15

HNO3

0.5

NH3

0.5

H2O2

0.5

HCHO

0.05

Table 6.3. overview of below cloud scavenging coefficients for gases

 

 

 

 



[1] note that if it is possible for a component to return from the aqueous phase to the atmosphere, the concentration change due to wet deposition d(l) can be negative and Cgas can increase