evaluation of hazardous sites in baden - württemberg
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Evaluation of hazardous Sites in Baden - Württemberg. Referat 44 – Altlasten, Schadenfälle Dr. Rolf Hahn Landesanstalt für Umwelt, Messungen und Naturschutz Baden-Württemberg Griesbachstraße 1 76185 Karlsruhe [email protected] Tel.: (0721)5600-1212 Fax: -1521. - PowerPoint PPT PresentationTRANSCRIPT
Referat 44 – Altlasten, SchadenfälleDr. Rolf Hahn
Landesanstalt für Umwelt, Messungen und
Naturschutz Baden-Württemberg
Griesbachstraße 1
76185 Karlsruhe
Tel.: (0721)5600-1212 Fax: -1521
Evaluation of hazardous Sites in
Baden - Württemberg
Seite 2, xxxx.2006
Area: 120 km2
Historical investigation finished in 2002(Proceedings in 5 years) study of files evaluation of aerial photographs viewing of location
7.700 Industrial Sites3.300 Waste dump Sites
Results
82.000 Sites (waste dump sites and hazardous abandoned industrial sites). Initial suspicion confirmed for 11.000 Sites (= 20 %)Considerable entry of contaminant into the soil are expected
Evaluation of hazardous Sites in Baden-Württemberg
Seite 3, xxxx.2006
no contaminated site
no contaminated site
no contaminated site
no contaminated siteno contaminated site
no contaminated siteno contaminated site
no contaminated siteno contaminated site
Risk assessment in several steps
Seite 5, xxxx.2006
Assessment
Orientation investigation
Assessment
Detail investigation
Assessment
Immediate measures to ward Hazards
Contaminated site
site still under suspiction to be contaminated
site under suspiction to be contaminated
no contaminated site
no contaminated site
no contaminated site
Supervision by Authorities
Immediate measures to ward Hazards
Supervision by Authorities
Immediate measures to ward Hazards
Supervision by Authorities,Self-Monitoring
Risk assessment
Seite 6, xxxx.2006
Remedial investigation Remediation plan
Remediation /protection and restriction measures
Self- Monitoring after Remediation/
Protection and restriction measuresSupervision by Authorities,
Self- Monitoring
Remediation and Monitoring
Seite 7, xxxx.2006
Distinguish between the different environmental
resources to be protected groundwater
surface water
soil
air
Aim: expand knowledge about a site in each step set of priorities
eliminate sites from process
Seite 8, xxxx.2006
Historical investigation: risk assessmentMinimum information type of area community address field name (register of lands) geographical coordinates
Information for the way of acting business negative list: e.g..
pharmacy
plumbing
shoemaker
Seite 9, xxxx.2006
type of dump site, type of industry
active time period
business specific contaminants
accidents
interruption times
area use
Information for the set of priorities (ranking) hazard of the material
environmental persistance
point of assessment
matrix effects
importance of the resource to be protected
Seite 10, xxxx.2006
The data set can be found generally in archives: aerial photography (allied flights) city maps, topography maps on-site work business registration address lists (street names often changes)
Orientation investigation initial systematic measurements
related resources to be protected
Next step
Seite 11, xxxx.2006
Suspicion facts and sample points
Galvanik
Faßlager
Whs
Flstk 1793
Flstk 1791
Straße
Whs
Flstk 1793
Flstk 1791
Straße
Tank-stelle
Verdacht Verdacht kein Verdacht
Schrottplatz
electroplating plant
barrel depot
house
Flstk 1793
Flstk 1791
Road
house
Flstk 1793
Flstk 1791
Road
gas station
locatable not locatable no suspicion
scrap yard
Case 1Herd of pollutant locatable
Case 2 Spatial not locatable refuse dump suspicion
Seite 12, xxxx.2006
hazard of material (site-independent value) ro
based on toxicological, physical, chemical, geolocial and environmental criteriamultiplier m to account for risk enhancement or reduction effects of local factors
m-values range from -0,5 to +1,5 with 1,0 equal to “environmentally neutral”
- relative procedure
- 5 steps
Principle of Evaluation (Ranking)Risk for need of action is joined with the risk after priority setting
Seite 13, xxxx.2006
environmental persistance rI = ro x mI
(transport in the unsaturated Zone)
point of assessment , i. e. the entry of contaminants to the resource (threshold or trigger values are exceeded) rII = rI x mII
matrix effects regarding the transport of contaminants (hydrogeological) rIII = rII x mIII
importance of the resource rIV = rIII x mIV
(water resource area)
Because of the soil protecting law from 1999 we have divided our system in the 2 parts
- need of action (see legal text)
- ranking (see the principles above)
Seite 15, xxxx.2006
Manual „Use of On-Site Analytic“ in 2001
Main tasks of the manualThe manual for the use of on-site analytical systems on contaminated
sites is to provide• time-saving and cost-effective strategies for investigation and
monitoring programmes;• expert help in deciding on suitable technology options to be taken
for specific applications;• quality assurance standards and measures to achieve
reproducable results;• a transparent and comprehensive planning concept for
investigation programmes including on-site analysis.
First experiences on test-sites in Baden-Württemberg since 1987
Seite 16, xxxx.2006
Applications for on-site analysisBy using on-site analysis it is possible to accelerate investigation processes and combine several investigation
steps by immediate on-site evaluation; to define limits of centres of contamination more accurately and provide
a subtly differentiated classification of excavated material, while avoiding additional costs;
to control the direction of investigation or remediation technique; to exhaust the full cost reduction potential in all phases of investigation,
long-term monitoring and remediation.
Seite 17, xxxx.2006
Q u a lity a s s u ra n ce
D y n a m ic w o rkp la n
L is t o f av a ila b lein s tu rm e n ts
M e a s u rin gp rin c ip a l
C a s e s tu d ie s
D o k u m e n ta tio n
D a ta q ua lityo b je c tiv e s
S tra te g y
R e m e d ia t io n
Accident analysis
Maintenance ofindustrial health and
safetystandards
Appendix:
Investigation
TasksMonitoring
Seite 18, xxxx.2006
Definition: measurement of analytical data, on-site and outside chemical laboratories; immediately or within a short times.
Practical relevance: low-cost methods; simple
Focus: portable analyses and sensors/ probes (field photometers, PID, FID, EIA, XRF)
Basic principles
Seite 19, xxxx.2006
on-site ana lysis
w ith sam p ling w ithou t sam p ling
m ob ile ana lys is
portab le ana lyse r
sensors / p robes
und istu rb ing m ethods
On-site analysis - Methods and types
Seite 20, xxxx.2006
Parameter (1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12) (13)
Heavy metals
Mercury
Anions
Cyanides
Gases (O2, CO2,
NOX,...)
PAH
Hydrocarbons
BTEX
vCHC
PCB
PCP
Legend: Grey: Application is possible Hatched: mobile laboratory analysis (elaborate and expensive)
ind
icat
or
test
s
imm
un
o a
ssay
tes
t ki
ts
Tes
t ki
ts
gas
tes
tin
g t
ub
e
gas
sen
sors
flam
e / p
ho
toio
nis
atio
n
det
ecto
r (P
ID/F
ID)
UV
sp
ectr
osc
op
y
thin
-lay
er
chro
mat
og
rap
hy
X-r
ay f
luo
resc
ence
(X
RF
)
Ion
mo
bili
ty
spec
tro
sco
py
(IM
S)
IR s
pec
tro
sco
py
GC
Mas
s sp
ektr
os c
op
y (G
C-M
S)
Ato
mic
ab
sorp
tio
n s
pec
tr
osc
op
y (A
AS
)
Gas
ch
rom
ato
gra
ph
y (G
C)
Seite 21, xxxx.2006
Strategy Chart
Criteria which are taken into consideration
the required quality of the measuring results
the instrument-specific properties
The strategy is an iterative process
Individual planning stages can be repeated several times.
Application Strategy
Seite 22, xxxx.2006
Qua
lity
assu
ranc
e
D a ta qua lity ob jec tives
D ocu m e nta tion
P urpose & ob jectives
Dyn
am
ic w
ork
pla
n
S ele ction o f te chn o lo gy
S am p lin g Q A
S am p lin g
O rg a n isatio n a l &te ch n ica l re a lisa tio n
Q A fo r a na lytic
S ite ow ne r,adm in istra tion/re gu la tory ag encies
S ite ow ne r,adm in istra tion/re gu la tory ag encies
A pprova l by s ite ow ne r, a dm in istra tion/re gu la tory ag encies
Strategy chart for the application of on-site analysis
Seite 23, xxxx.2006
There are 5 main categories of tasks:
Investigation:
Determination of pollution and spatial distribution in the soil using random or selected investigation grid patterns.
Accident analysis:
Determination of spatial distribution (extension) and mobility of a known pollutant taking into account any given time limits.
Application area
Seite 24, xxxx.2006
Maintenance of industrial health and safety standards:
Determination of the concentration of a pollutant and its time-related distribution with due consideration to the specific industrial safety requirements.
Long-term monitoring:
Long-term monitoring of contaminated sites or remediation acitivities, for example, specialised technical monitoring following remediation work or monitoring of long-term measures, such as the removal of soil gas by means of suction.
Remediation:
Activities to support the monitoring of remediation and safety measures, such as the control of material flows or soil treatment systems, within a specified timeframe.
Seite 25, xxxx.2006
Selection of equipment
In addition with Annex 2 of the manual (equipment data) pre-selections are possible
Com parison of technica l data
Contam inants of concern, screeningparam eter or quantitative analysis
Detection lim its,analytical accuracy
Purpose & objectives
Data quality ob jective &dynam ic work p lan
Costsstaff & equipm ent
F inancia l background
Practicabilitym obility, a tm ospheric conditions,
throughput rates
Dem ands on staff Availab ility, qualification
Site specific conditions,ED P
Selection of fie ld instrum ents
List o f technica lequipm ent
Selection of appropriate field instruments
Dynamic work plan
Seite 26, xxxx.2006
sam pling strategy, defin ition of investigation and sam pling techniques
fixing sam pling points:regard ing contam ination suspicious sites grid system (square, triangular, po lar, linear)sequence of sam pling, steering investigation d irection
protocol o f sam pling activity:which tem plate sheet should be used?distribution of the protocol?
sam pling m ethod:results d irectedm ixed sam ples/seperate sam plesquantity o f sam pling m ateria l
sam ple preparation:hom ogenising, chem ical extractions, ...
analysing and in terpretation of results
reaction on base of the analytica l results
fee
dba
ck /
bac
k co
up
ling
Sampling
Criteria for sampling planning and procedure