Solec_presentation_TIMBRE meeting [tryb zgodności]

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Solec_presentation_TIMBRE meeting [tryb zgodności]
Tereny zdegradowane w Solcu Kujawskim
– teren testowy dla projektu TIMBRE
Degraded terrains in Solec Kujawski
– test area for the TIMBRE project
Dr Wojciech Irmiński, Geo-Logik, Poland
Rewitalizacja terenów zdegradowanych w Polsce – dobre praktyki
TIMBRE i Urząd Marszałkowski Województwa Lubuskiego
Zielona Góra, 28.03.2012
The localisation
HOMBRE case study with sub-areas
Former
manufactory
HOMBRE case
studyimpregnation
with sub-areas
(1876 – 2001), demolished,
abandoned area, heavy
City forest with regional
contaminated ground (sands) and
attraction – Jura Park. Many
groundwater (4,5 m depth) - PAHs,
visitors and excursions per
BTEX, Phenols
day. Open air museum, sport
facilities, restaurants
Housing estate (blocks),
school, shops.
Metal & car industry,
heating plant and
railway area.
Production and
storage area.
Forest and small creek
Currently shoe manufactory.
Former tannery with spill ponds,
Cr, Sn and As contamination is
possibile
The current situation
Mapa geodezyjna z istniejącym
stanem zabudowy oraz hałdami
ziemi i gruzu
Objaśnienia:
Soil and debris dumps
murowany podpoziomowy zbiornik
zrzutowy oleju impregnacyjnego
ruiny piwnic i fundamentów
budynków produkcyjnych
Half-full creosote
container, partly cut
W
E
S
dawny budynek transformatora
ucięty zbiornik stalowy nadpoziomowy
Demolished basements
N
murowany fundament Ŝurawia
hałdy gruzowo-ziemne
(kontury przybliŜone)
100 m
The current situation
Half-full creosote container, partly cut is
the most dangerous source of
contamination.
Old basement used as big underground
creosote container – for the emergency
situation (e.g. fire)
The debris material – have to be selected and reused
Degraded surface and several waste dumps
(incl. dangerous waste)
Dumps of contaminated ground and
debris:
• unable base remediation and land
redevelopment;
• there are a secondary grounds’ and
waters’ contamination source;
Deserted area is full of
rubbish and traces left by
unauthorised people who
entered the area
Main issue – contamination of soil and groundwater
Distinct vertical border
of contaminated soil
Concentration of PAH in soil and in groundwater– test results
from 2010 (accord. to INOCRE and RAMBOLL)
Zmiana koncentracji WWA w próbkach gruntu
7000
6200
6200
5000
6200
5730
6000
6160
5710
5320
5130
4720 4900
4570
4000
3000
2000
905
1000
0
Lizymetr I
t=0
Lizymetr II
t=2 tygodnie
t=4 tygodnie
Lizymetr III
t=8 tygodni
koncentracji WWA w próbkach wody
PAH Zmiana
concentration
in water versus time
12000
Suma WWA [µg/l]
Suma WWA [mg/kg s.m.]
PAH concentration in soil versus time
10000
10800
10300
9590
9030
8550
8550
8320
7230
8000
6260
5510
5380
6000
4480
4000
2000
0
The autochthonous bacteria from
Solec which is the PAH-killer
Lizymetr I
t=0
Lizymetr II
t=1,5 tygodnia
t=4 tygodnie
Lizymetr III
t=8 tygodni
The remediation concept for brownfields (2010)
Mapa dokumentacyjna do projektu
rekultywacji terenu po nasycalni
N
Objaśnienia:
Staff container
kontenerowy
kompleks socjalny
Container for fermentation
W
E
kontenerowy kompleks fermentatora
The soil
exchange
obszar
wymiany
gruntu
area
poletka bioremediacyjne
The bioremediation fields
ogrodzenie
(ponds)terenu prac (opcja pełna)
ogrodzenie terenu prac (opcja minimum)
The perimeter fence
studnia
depresjonująca
Depression
wells
piezometr
Piezometers
Thegruzu
dumps
of rubble
hałdy
do kruszarki
crusher
biopryzma
The bioprism
after
S
100 m
The soil monitoring works: May-October 2011
The soil monitoring works: May-October 2011
The remediation concept for brownfields – new version
Staff container
Container for fermentation
The soil exchange area
Soil washing instalation
The bioremediation fields (ponds)
The perimeter fence
Depression wells
Piezometers
The dumps of rubble after crusher
The bioprism
Dec. 2011
Assumptions and calculations
of hydrogeological model
(accord. to Madflow software)
www.zerobrownfields.eu
Hydrogeological model of
activity of the dewatering well
www.zerobrownfields.eu
The remediation concept for brownfields – the newest version
Staff container
Container for fermentation
The soil exchange area
Soil washing instalation
The bioremediation fields
(ponds)
The perimeter fence
Depression wells
Piezometers
The old wells (non existing)
The dumps of rubble after
crusher
The bioprism
Jan. 2012
Projected piezometers and wells
Investigation of possibility of waste disposal using thermic method
(alternative fuel for cement kilns)
Contents of heavy metals in ashes after
cineration of waste sample (according to the
firm SITA STAROL’s test – January 2012)
Co
9 ppm
Cu 142 ppm
Hg
0,5 ppm
Mn 155 ppm
Cd <0,1 ppm
Pb 72 ppm
As 10,5 ppm
Tl <0,1 ppm
Cr 50 ppm
Ni 15 ppm
HOMBRE and TIMBRE cooperation in the Solec case study
According the first field visit in Solec –
Nov.2011 – UFC (TIMBRE Project Partner) has
decided to conduct his field test of soil washing
on the brownfield area in Solec
In-situ Washing
Air
comp.
X
Areas made
waterproof to
prevent accidental
leakage
X
Storage
tank
Trap
Hydraulic connexions
Inject
tank
Hut
Vaccum
pumps
Heat.
Unit
Cool.
Unit
Sep.
Unit
Electric connexions
Waste
Storage
tank
The
visualisation
of potential
migration
paths
(for TIMBRE
team)
made by Geo-Logik
Jan. 2012
What now?
• Solec Kujawski has all required documents needed
to conduct remediation works
• Remediation project was already accepted by
authorities. The project includes using optimal
technologies (”technology
technology train”)
train
• Land’s owner applied for funding for land’s
remediation
• Currently, we are expecting final decision in March
2012.
The final view
Thank you for the attention

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