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Water chemistry
Cenflumarin – 4MT 2015
Teacher: Nathalie Verelst
Water chemistry partners
Water chemistry sampling sites
Methodology
• First we compare our data to last years data of
measurements around the school.
• Then we compare our test strip data to the
Walhorn, Emajõgi, Lake Melliste and Luutsna
datasets.
• We try to identify the land use around the
water body to explain the values.
T, S, ρ
• 2015 is warmer than
2014
• If S↑ → ρ ↑
• Measurement of S in the
Scheldt river might have
been less accurate.
• The dock is a lot less
saline, but it had rained a
lot before the
measurement.
0
5
10
15
20
25
30
35
Scheldt Pond Dock
T in °C 2014 T in °C 2015
S in PSU 2014 S in PSU 2015
Density in mg/cm³ 2014 Density in mg/cm³ 2015
pH, GH, KH
0
2
4
6
8
10
12
14
16
18
20
Scheldt Pond Dock
pH strips pH titration GH strips KH strips KH titration
• pH (titration) is slightly alkaline than
the pond or the dock. This is
because the Scheldt is more saline.
• KH is the same
• GH is higher in the pond and dock
because water is not moving, i.e.
there is more uptake of CO2 at the
surface.
• Titration is the most accurate type
of testing
• In comparison to 2014, the water
has become a lot harder, it can now
more easily bind with an acid an this
will lower pH (see also the graph on
the next slide).
CO2 & O2
• Before the water was
more alkaline, though it
contained a lot more CO2.
• With the rise of
temperature, primary
production consumed a lot
of CO2 and a bit of O2 .
• The dock became less
alkaline because of mixing
with the Scheldt river.
0
5
10
15
20
25
30
35
40
45
Scheldt Pond Dock
02 in mg/l 2014 O2 in mg/l 2015 CO2 in mg/l 2014
CO2 in mg/l 2015 KH in °d 2014 KH in °d 2015
pH 2014 pH 2015
NO3, NO2 & NH4
0
5
10
15
20
25
Scheldt pond dock
20
25
9
NO3 2014 titration NO3 2015 titration NO3 2015 strips
NO2 2014 titration NO2 2015 titration NO2 2015 strips
NH4 2014 titration NH4 2015 titration
• In 2015 we have less
ammonia in the Scheldt,
pond & dock.
• In 2015 chemical oxidation
of NO3 into NO2 was more
pronounced in the Scheldt
river.
• The amonium level clearly
dropped in 2015. This might
indicate a population of
decomposers in anaerobic
circumstances in the
benthos.
PO4
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
Scheldt river Middlepond Dock
2014 2015
• There has been an
increase of PO4 between
2014 & 2015. This
increase is more
pronounced in the dock
and pond because
circulation is low. The
dock & pond are also
connected. The most
likely source of PO4 is the
increase of nutrient load
in the Scheldt river.
Copper
• In 2014 the lock was
permanently closed
and the water stayed
on the same place
and there was a lot of
oil pollution. Recently
the lock has been
repaired and all
values are just within
normative values
(norm = 0.1 mg/l).
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
0.18
0.2
Scheldt river Middlepond Dock
Cu_2014
Cu_2015
T, S, ρ
• Conductivity measurements
at respective temperatures
were converted to psu.
• The Scheldt river,
Cenflumarin dock and pond
are brackish. If S↑ → ρ ↑
• Temperatures in Lake
Melliste and Luutsna river
are lower.
0
5
10
15
20
25
30
T in °C S in PSU Density in mg/cm³
pH, GH, KH
• Salty water is more alkaline than
fresh water.
• Orissaare has low hardness and
pH. The water will not easily bond
to an acid.
• The hardest water is found in
rivers that flow through mineral
rich geological regions.
• Cenflumarin pond has a relatively
high nutrient content and low
uptakem the water will therefore
be more likely to bond to an acid.
• Luutsna river has unusually low
carbonate hardness.
-2
3
8
13
18
23
pH GH KH
NO3, NO2, NH4
• Nitrates are higher in
agricultural zones and in rivers
that flow through agricultural
zones.
• When it becomes warmer
they form toxic nitrites.
Titration of nitrites led to a
false positive in the Scheldt
river (NO2 high, T low), what
about Emajõgi river?
• Decomposers can break down
poisionous nitrites into NH4,
though their productivity is
low. NH4 was not measured in
Estonia.
0
5
10
15
20
25
30
35
40
45
50
NO3
NO2
NH4
Conclusion
• It would be interesting if all partners could have measured
temperature, salinity, O2 and CO2 – content.
• The values in the Cenflumarin dock changed significantly from
2014 untill 2015 because the lock connecting the dock to the
Scheldt river has been reopened.
• The Walhorn sites suffer from a high nutrient load from
agriculture, for Emajogi river we should consider not only the
nutrient load, but also the temperature. In cold conditions,
there will be no nutrient uptake.
• We were wondering whether the high nitrite value for nitrites
in Emajõgi river was not a false positive, since no nitrates are
present. Lake Melliste seems a rather clean water body.

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Water chemistry

  • 1. Water chemistry Cenflumarin – 4MT 2015 Teacher: Nathalie Verelst
  • 4. Methodology • First we compare our data to last years data of measurements around the school. • Then we compare our test strip data to the Walhorn, Emajõgi, Lake Melliste and Luutsna datasets. • We try to identify the land use around the water body to explain the values.
  • 5. T, S, ρ • 2015 is warmer than 2014 • If S↑ → ρ ↑ • Measurement of S in the Scheldt river might have been less accurate. • The dock is a lot less saline, but it had rained a lot before the measurement. 0 5 10 15 20 25 30 35 Scheldt Pond Dock T in °C 2014 T in °C 2015 S in PSU 2014 S in PSU 2015 Density in mg/cm³ 2014 Density in mg/cm³ 2015
  • 6. pH, GH, KH 0 2 4 6 8 10 12 14 16 18 20 Scheldt Pond Dock pH strips pH titration GH strips KH strips KH titration • pH (titration) is slightly alkaline than the pond or the dock. This is because the Scheldt is more saline. • KH is the same • GH is higher in the pond and dock because water is not moving, i.e. there is more uptake of CO2 at the surface. • Titration is the most accurate type of testing • In comparison to 2014, the water has become a lot harder, it can now more easily bind with an acid an this will lower pH (see also the graph on the next slide).
  • 7. CO2 & O2 • Before the water was more alkaline, though it contained a lot more CO2. • With the rise of temperature, primary production consumed a lot of CO2 and a bit of O2 . • The dock became less alkaline because of mixing with the Scheldt river. 0 5 10 15 20 25 30 35 40 45 Scheldt Pond Dock 02 in mg/l 2014 O2 in mg/l 2015 CO2 in mg/l 2014 CO2 in mg/l 2015 KH in °d 2014 KH in °d 2015 pH 2014 pH 2015
  • 8. NO3, NO2 & NH4 0 5 10 15 20 25 Scheldt pond dock 20 25 9 NO3 2014 titration NO3 2015 titration NO3 2015 strips NO2 2014 titration NO2 2015 titration NO2 2015 strips NH4 2014 titration NH4 2015 titration • In 2015 we have less ammonia in the Scheldt, pond & dock. • In 2015 chemical oxidation of NO3 into NO2 was more pronounced in the Scheldt river. • The amonium level clearly dropped in 2015. This might indicate a population of decomposers in anaerobic circumstances in the benthos.
  • 9. PO4 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 Scheldt river Middlepond Dock 2014 2015 • There has been an increase of PO4 between 2014 & 2015. This increase is more pronounced in the dock and pond because circulation is low. The dock & pond are also connected. The most likely source of PO4 is the increase of nutrient load in the Scheldt river.
  • 10. Copper • In 2014 the lock was permanently closed and the water stayed on the same place and there was a lot of oil pollution. Recently the lock has been repaired and all values are just within normative values (norm = 0.1 mg/l). 0 0.02 0.04 0.06 0.08 0.1 0.12 0.14 0.16 0.18 0.2 Scheldt river Middlepond Dock Cu_2014 Cu_2015
  • 11. T, S, ρ • Conductivity measurements at respective temperatures were converted to psu. • The Scheldt river, Cenflumarin dock and pond are brackish. If S↑ → ρ ↑ • Temperatures in Lake Melliste and Luutsna river are lower. 0 5 10 15 20 25 30 T in °C S in PSU Density in mg/cm³
  • 12. pH, GH, KH • Salty water is more alkaline than fresh water. • Orissaare has low hardness and pH. The water will not easily bond to an acid. • The hardest water is found in rivers that flow through mineral rich geological regions. • Cenflumarin pond has a relatively high nutrient content and low uptakem the water will therefore be more likely to bond to an acid. • Luutsna river has unusually low carbonate hardness. -2 3 8 13 18 23 pH GH KH
  • 13. NO3, NO2, NH4 • Nitrates are higher in agricultural zones and in rivers that flow through agricultural zones. • When it becomes warmer they form toxic nitrites. Titration of nitrites led to a false positive in the Scheldt river (NO2 high, T low), what about Emajõgi river? • Decomposers can break down poisionous nitrites into NH4, though their productivity is low. NH4 was not measured in Estonia. 0 5 10 15 20 25 30 35 40 45 50 NO3 NO2 NH4
  • 14. Conclusion • It would be interesting if all partners could have measured temperature, salinity, O2 and CO2 – content. • The values in the Cenflumarin dock changed significantly from 2014 untill 2015 because the lock connecting the dock to the Scheldt river has been reopened. • The Walhorn sites suffer from a high nutrient load from agriculture, for Emajogi river we should consider not only the nutrient load, but also the temperature. In cold conditions, there will be no nutrient uptake. • We were wondering whether the high nitrite value for nitrites in Emajõgi river was not a false positive, since no nitrates are present. Lake Melliste seems a rather clean water body.

Editor's Notes

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