TEXTE Environmental Impacts of Exhaust Gas Cleaning Systems for Reduction of SOx on Ships — Analysis of status quo
Report compiled within the framework of the project ImpEx
> Particularly, missing and unsuitable sampling points are reported
7.4.2 Chemical composition
Based on the results of the abovementioned studies the following general observations and
conclusions can be stated regarding the chemical composition of EGCS discharge water:
Trace metals are mainly found in dissolved form. This could be explained by acidic
conditions and high levels of chloride in the water. Removal efficiency of metals relying only
on mechanical treatment is therefore limited.
Significant enrichment of vanadium and nickel in discharge water is observed. Both metals
are found in residual fuel oils in high concentrations.
Copper and zinc were also found in relevant concentrations in water samples (even in inlet
samples). The materials of the sampling pipe, corrosion protection and antifouling systems
may explain those irregularities.
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D-
Nitrate levels in discharge water were generally found below the IMO discharge limit
concentration and strongly dependent of the inlet water levels. Nitrite levels in OL samples
were considered negligible.
Dil concentration in OL discharge water was below 1 ppm, while oil in CL discharge water
ranged between 2 -21 ppm (see Table A-4).
Relation between oil content and PAHyne was assessed only by one research study. That
study found a correlation between the parallel measurements of PAHyne and laboratory
results for oil content (HOI) and PAHgpa16. The PAHpne values from the on-line monitoring
data did not show a correlation with oil nor PAHgpra16. The use of PAHypne as a proxy
parameter for oil content in EGCS discharge water should be further examined.
Relation between turbidity, suspended solids, organic pollutants and metals was not
assessed by any research work. The use of turbidity as criteria and proxy parameter for
pollutants in EGCS discharge water should be examined.
PAHera16 cConcentrations in discharge water were generally found below the IMO limit value
given in PAHyne (this comparison is actually not consistent but serves to illustrate the PAH
levels in EGCS discharge water).
Naphthalene, phenanthrene and fluorene represented the highest fractions of the PAHepa16.
PAHs with more rings were found in much lower levels, mainly below the detection limits. In
CL discharge water samples, however, their presence was more notable even though the
water treatment unit could remove them very efficiently.
Petrogenic PAHs (fuel related) were more dominant in the discharge water rather than
pyrogenic PAHs (combustion related).
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