management of contaminated groundwater in the netherlands › 3 › i9823en › i9823en.pdf ·...

1
GLOBAL SYMPOSIUM ON SOIL POLLUTION 2 - 4 MAY 2018 | FAO - ROME, ITALY Management of contaminated groundwater in the Netherlands Margot de Cleen and Co Molenaar Ministry of Infrastructure and Water Management, Rijkswaterstaat, Environment INTRODUCTION Industrial areas often have to deal with histori- cal (before 1987) contamination of land and groundwater. Over time the contamination has spread over sometimes considerate areas. “Plumes” of different polluters have become mixed, polluters cannot always be identified and sometimes are not even alive. Consequently the liability of the “polluter pays principle” is hard to execute. Also in case of transfer of responsi- bility to a “new” site owner the problem of mixed plumes makes it hard to define the liability. How to solve this liability dilemma and find sustainable alternatives? METHODOLOGY Public authorities should take the lead Mixed remediation strategies required Mega Site Rotterdam Harbour Historical contamination; The quality of the groundwater exceeds the intervention values for groundwater; • The volume of affected groundwater is over 6.000 m3 and the annual increase in volume is over 1.000 m3; There is a layer of contaminants on top or below the aquifer; • Relation to vulnerable objects, defined accord - ing to the source-path-receptor model (water supply for human consumption, process water for industry or a protected area in accordance with the EU Water Framework Directory. Bottlenecks Urban areas often contain large mixed plumes; Liability is unclear; • Technical or cost effective solutions are com- plicated since plumes are located under city centers; Incentives to remediate lack; • Dispersion of the contamination is influenced by the use of the subsoil; Municipalities want to make an integrated assessment when developing an urban area. Therefore a change in addressing the liability is needed and an incentive to achieve the pol- icy goal to manage the risks of historical ground- water contamination. Trust in finding a joint solution is needed to solve the problem of mixed plumes Remediation Strategy From a site approach towards an integral area approach; Restricted to historical contamination!! Con- tamination originating after 1987 must be remediated directly by polluter; Risk management in stead of remediation on an area level; Monitoring on the border of the area; if nec- essary take remediation measures at borders or plane of compliance; Dispersion within the area is allowed; the qual- ity of the groundwater must comply the use. Cost reduction 50% (average). Going to court takes time, money and offers no guarantees Policy and stakeholder perspectives: the deal The site owner can transfer the liability to a public authority In exchange the owner: Remediates the source; Pays redemption money; Free riders have to remediate all. The local authority can manage the risks and develop areas In exchange the authority : Organizes the monitoring; Organizes the data management; Organizes the funding and a calamity fund. Other stakeholders have the certainty that their assets are safe and new developments can take place In exchange they: Contribute in the management and mainte- nance; Supply data and knowledge. Model future impacts The mega site characterization provides all basic information that is required to predict the impact of contaminants to the receptor and to deter- mine the effectiveness of risk management sce- narios. The mega site characterization carried out for the Rotterdam harbour area comprises the assessment of: the contaminant distribution, geohydrology and natural attenuation. Measures are source removal, pump and treat, enhanced natural attenuation, isolation and monitoring. CONCLUSIONS Solving the problem of mixed plumes asks for: Action: reverse trend by source remediation; Collaboration; Transfer of liability to a public organization; Tight agreements and “free rider prevention”; Site knowledge and area approach; Monitoring; • Calamity plan with secured financing. 8.8 3.6 0,7 1.6 2.6 0.3 8.8 5.8 1.6 2.6 0.3 8.8 3.6 1.6 2.8 0.3 0 2 4 6 8 10 12 14 16 18 20 M€/year Mixed strategy A Mixed strategy B Mixed strategy C monitoring POC3 isolation monitoring POC2 ENA P&T source measures (17.5) (19) (17) Effect of mixed strategy (impact on 3rd plane of compliance) 0 2 4 6 8 10 12 1980 2000 2020 2040 2060 2080 2100 % of length impacted above Ivalue Autonomous mixed strategy A mixed strategy B mixed strategy C active measures start in 2005 13.3 M€/y 13.3 M€/y 14.9 M€/y Scenarios

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Page 1: Management of contaminated groundwater in the Netherlands › 3 › I9823EN › i9823en.pdf · POLLUTION 2 - 4 MAY 2018 | FA O - ROME, ITAL Y Management of contaminated groundwater

G L O B A L S Y M P O S I U MO N S O I L

P O L L U T I O N2 - 4 M A Y 2 0 1 8 | F A O - R O M E , I T A L Y

Management of contaminated groundwater in the Netherlands

Margot de Cleen and Co MolenaarMinistry of Infrastructure and Water Management, Rijkswaterstaat, Environment

INtRoduCtIoN

Industrial areas often have to deal with histori-cal (before 1987) contamination of land and groundwater. Over time the contamination has spread over sometimes considerate areas. “Plumes” of different polluters have become mixed, polluters cannot always be identified and sometimes are not even alive. Consequently the liability of the “polluter pays principle” is hard to execute. Also in case of transfer of responsi-bility to a “new” site owner the problem of mixed plumes makes it hard to define the liability. How to solve this liability dilemma and find sustainable alternatives?

MEthodology

Public authorities should take the leadMixed remediation strategies required

Mega Site Rotterdam Harbour• Historical contamination;• The quality of the groundwater exceeds the

intervention values for groundwater;• The volume of affected groundwater is over

6.000 m3 and the annual increase in volume is over 1.000 m3;

• There is a layer of contaminants on top or below the aquifer;

• Relation to vulnerable objects, defined accord-ing to the source-path-receptor model (water supply for human consumption, process water for industry or a protected area in accordance with the EU Water Framework Directory.

Bottlenecks• Urban areas often contain large mixed plumes;• Liability is unclear;• Technical or cost effective solutions are com-

plicated since plumes are located under city centers;

• Incentives to remediate lack;• Dispersion of the contamination is influenced

by the use of the subsoil;• Municipalities want to make an integrated

assessment when developing an urban area.

Therefore a change in addressing the liability is needed and an incentive to achieve the pol-icy goal to manage the risks of historical ground-water contamination.

Trust in finding a joint solution is needed to solve the problem of mixed plumes

Remediation Strategy• From a site approach towards an integral area

approach;• Restricted to historical contamination!! Con-

tamination originating after 1987 must be remediated directly by polluter;

• Risk management in stead of remediation on an area level;

• Monitoring on the border of the area; if nec-essary take remediation measures at borders or plane of compliance;

• Dispersion within the area is allowed; the qual-ity of the groundwater must comply the use.

Cost reduction 50% (average).

Going to court takes time, money and offers no guarantees

Policy and stakeholder perspectives: the dealThe site owner can transfer the liability to a public authorityIn exchange the owner:• Remediates the source;• Pays redemption money;• Free riders have to remediate all.The local authority can manage the risks and develop areasIn exchange the authority :• Organizes the monitoring;

• Organizes the data management;• Organizes the funding and a calamity fund.Other stakeholders have the certainty that their assets are safe and new developments can take placeIn exchange they:• Contribute in the management and mainte-

nance;• Supply data and knowledge.

Model future impactsThe mega site characterization provides all basic information that is required to predict the impact of contaminants to the receptor and to deter-mine the effectiveness of risk management sce-narios. The mega site characterization carried out for the Rotterdam harbour area comprises the assessment of: the contaminant distribution, geohydrology and natural attenuation. Measures are source removal, pump and treat, enhanced natural attenuation, isolation and monitoring.

CoNClusIoNs

Solving the problem of mixed plumes asks for:• Action: reverse trend by source remediation;• Collaboration;• Transfer of liability to a public organization;• Tight agreements and “free rider prevention”;• Site knowledge and area approach;• Monitoring;• Calamity plan with secured financing.

8.8

3.6

0,71.6

2.60.3

8.8

5.8

1.6

2.60.3

8.8

3.6

1.6

2.80.3

0

2

4

6

8

10

12

14

16

18

20

M€/year

Mixed  strategy  A Mixed  strategy  B Mixed  strategy  C

monitoring  POC3isolationmonitoring  POC2ENAP&Tsource  measures

(17.5) (19) (17)

Effect  of  mixed  strategy(impact  on  3rd  plane  of  compliance)

0

2

4

6

8

10

12

1980 2000 2020 2040 2060 2080 2100

%  o

f  len

gth  

impa

cted

 abo

ve  I-­

valu

e

Autonomous  

mixedstrategy  A

mixedstrategy  B

mixedstrategy  C

active  measures  start  in  2005

13.3  M€/y

13.3  M€/y

14.9  M€/y

Scenarios