1. General information
Location and description of the intervention
City or FUA
Utrecht
Region
Europe
Native title of the NBS intervention
Biowasmachine
Short description of the intervention
The Bio Washing Machine is a combination of an Aquifer Thermal Heat Storage (ATES) system and biological natural attenuation of groundwater and is thereby mainly focused on groundwater decontamination and energy storage. The ATES system accelerates the biological degradation of groundwater contamination and provides sustainable energy because cold water is pumped through buildings during the summer to cool the buildings and hot water during winter for heating. The groundwater decontamination measurements are aimed at protecting water in order to provide safe drinking water (ref. 1, 2, 3)
Address

Stationshal
12
3511 CE Utrecht
Netherlands

Total area
900000.00m²
NBS area
900000.00m²
Type of area before implementation of the NBS
Please specify “other type of area” before implementation of the NBS
Utrecht central station area (ref. 1)
Timeline of intervention
Start date of the intervention (planning process)
2006
Start date of intervention (implementation process)
2009
End date of the intervention
2013
Present stage of the intervention
Goals of the intervention
Main objective: Decrease soil contamination which improves groundwater quality and allow the urban developments around the central station including construction activities (ref. 1)
Additional objectives:
- Providing sustainable energy (ref. 1, 3)
- CO2 reduction, as fossil fuels are no longer required to cool/heat buildings (ref. 1)
- Optimize monitoring of contamination in order to research the effects of ATES on soil decontamination (scientific goal) (ref. 1, 3)
- Cost reduction (as traditional groundwater contamination is more expensive) because the organic decontamination of groundwater takes a very long time because the contamination is unevenly spread and contaminated groundwater is not mixed with decontaminated ground water, which slows down the process. Because the ATES system accelerates the organic decontamination process, decontaminated groundwater no longer needs to be pumped and decontaminated which is very costly because a ground water pump should run for 20-30 years (ref, 1-4).
Quantitative targets
Total area of 90 ha of development includes the Bio Washing Machine (ref. 1)
Achieve contamination reduction in soil of depth 5-50 meters (ref. 8)
CO2 reduction of 6.000 tonnes/year (ref. 10)
Expected effects of ATES: reduction of VOC mass of 40% in subsurface (ref. 10)
7 million m3 ground water subtraction annually (ref. 11)
Cost reduction of 20 million euros (ref. 11)
Total amount of decontaminated that needs to be targeted is 50 million m3 (ref. 11)
Monitoring indicators defined
Mainly water quality indicators: oxygen (mg/l), EC (μS/cm), RedOx (mV) and pH (ref. 8)
Chemical substances, mainly chlorylcarbonhydrates (μg/l) (ref. 8)
Climate change adaptation: What were the goals of the NBS?
Climate change adaptation: What activities are implemented to realize the conservation goals and targets?
Please specify "other Type of NBS project"
Aquifer Thermal Energy Storage (ref. 1)
Implementation activities
ATES systems in new buildings surrounding Central Station of Utrecht (ref. 3)
Stimulating biological attenuation (by means of construction and addition of organic substances) (ref. 3)
Placement of 90 measurement tubes in Central Station area which measure the contamination concentration and bacterial population (ref. 3)
Groundwater cleaning using energy efficient machinery (ref. 1)
NBS domain and interventions
Ecological domain(s) where the NBS intervention(s) is/are implemented
Green areas for water management
Sustainable urban drainage systems
What is the level of innovation / development of the NBS related to water management?
Vegetation Type
Amenities offered by the NBS
Services
Expected ecosystem services delivered
Provisioning services
Water (surface and ground water for drinking and non-drinking purposes)
Regulating services
Local climate regulation (temperature reduction)
Air quality regulation
Water purification / filtration
Cultural services
Intellectual interactions (scientific and / or educational)
Scale
Spatial scale
Micro-scale: District/neighbourhood level
Beneficiaries
Please specify other local relevant strategy
Ground Water Policy of the Municipality of Utrecht: 'Beschermen, verbeteren en benutten: Naar een gebiedsgerichte aanpak grondwaterverontreinigingen in de ondergrond van Utrecht' (2009). (ref. 13)
The 'Soil, Water and Environment Plan' of the Province of Utrecht supports ATES systems in the province (ref. 14)
Governance
Governance arrangements
Please specify the roles of the specific government and non-government actor groups involved in the initiative
The initiating actors were the Municipality of Utrecht and Province of Utrecht. Utrecht Municipality is the main directing actor that initiated the NBS and monitors the process. Therefore, the NBS can be considered government-led. Another governmental actor involved is the Hoogheemraadschap Stichtse Rijnlanden (Water Body) who agreed upon the plan regarding their concern of water contamination. Non-governmental actors involved are businesses in and around the central station; Hoog Catherine BV, Corio Nederland BV, NS Poort Ontwikkeling BV and Prorail BV who signed a declaration of intent and are also investing in the project (5).
Also universities are involved, the University of Utrecht and the University of Wageningen who conduct research mainly regarding the functioning of the ATES in combination with soil decontaminatino and recommend the development of the Bio Washing Machine (ref. 4).
Key actors - initiating organization
Land owners
Key actors - Other stakeholders involved (besides initiating actors)
National government
Regional government
Local government/municipality
Non-government organisation/civil society
Private sector/corporate actor/company
Researchers/university
Land owners
Participatory methods/forms of community involvement used
Policy drivers
NBS intervention implemented in response to an Regional Directive/Strategy
Unknown
NBS intervention implemented in response to a national regulations/strategy/plan
Yes
Please specify the national regulations/strategy/plan
'Wet Bodembescherming' (Law of Protection). The Bio Washing Machine follows the cluster approach as defined in article 42 (ref. 11)
NBS intervention implemented in response to a local regulation/strategy/plan
Yes
Please specify the "local regulation/strategy/plan"
The Bio Washing Machine is part of the 'Sanitation Plan' of the Municipality of Utrecht ('Protection, Improvement and Usage') which is focused on local approach to ground water contamination (ref. 12, 13)
Mandatory or voluntary intervention
Voluntary (spontaneous)
Enablers
Presence of specific city-level GI/NBS vision/strategy/plan - mentioned in connection to the project
Yes
Please specify
Ground Water Policy of the Municipality of Utrecht: 'Beschermen, verbeteren en benutten: Naar een gebiedsgerichte aanpak grondwaterverontreinigingen in de ondergrond van Utrecht' (2009). (ref. 13). The Bio Washing Machine needed to fit this policy.
Presence of specific city-level GI/NBS section/part in a more general plan - mentioned in connection to the project
Unknown
If there is a relevant strategy or plan, please specify the theme / type of the plan.
Please specify other vegetation type
Unknown
Presence of city network or regional partnerships focused on NBS - mentioned in connection to the project
Yes
Please specify
The 'Soil, Water and Environment Plan' of the Province of Utrecht supports ATES systems in the province (ref. 14)
Presence of GI / NBS research project - mentioned in connection to the project
Yes
Please specify
CityChlor which is an EU INTERREG IVB initiative, which is a transnational cooperation between partners from Flanders, Germany, France and the Netherlands project on improving quality and reducing pollution of groundwater and soil (ref. 1,5,6)
Subsidies/investment for GI / NBS in the city - mentioned in connection to the project
Yes
Please specify
The project has received European Regional Development Funding through INTERREG IV B (ref. 1, 6)
Co-finance for NBS
Yes
Co-financing governance arrangements
Unknown
Was this co-governance arrangement already in place, or was it set up specifically for this NBS?
Financing
What is/was the Cost/Budget (EUR) of the NBS or green infrastructure elements?
Unknown
What are the total amount of expected annual maintenance costs?
Unknown
What is the expected annual maintenance costs of the NBS or GI elements?
Unknown
Please specify cost savings
Unknown
Please specify total cost (EUR)
10 million euros [4]
Non-financial contribution
Unknown
Which of the involved actors was motivated by this model?
Please specify technological innovation
ATES system, which provides sustainable energy by making use of the temperature of ground water. In summer, hot water from houses is stored in the ground water and in winter, this relatively hot ground water is pumped through the buildings to heat the buildings. In summer, ground water is relatively cold and pumped through to cool the buildings. As a result of the pumping mechanism, contaminated ground water is in motion which accelerates the decontamination process of bacteria in the soil. [3,4] Thereby, it is an integrated approach of decontamination and providing sustainable energy [3]
Please specify social innovation
The project is innovative because of the early cooperation and alignment between all actors involved in urban spatial planning and development [6]
Please specify novelty level of the innovation
It combines different techniques, particularly ATES and contamination which are implemented as synergy of providing sustainable energy and contamination (they support each other). The ATES makes the decontamination of ground water 10 times faster because the hot-cold storage increases speed of organic attenuation [3,4] The idea to combine soil energy with decontamination is not new, but applying this principle on a large scale in a dynamic urban environment is exceptional. [15]
Please specify Replicability/Transferability
The finding that there is a potential synergy between ATES and ground water contamination resulted in policy adaptation regarding ATES. At first, ATES was only applied to areas with uncontaminated ground water, but since the Bio Washing Machine it can also be applied to areas with contaminated ground water and the targets of temperature of ground water where ATES could be applied are also adjusted [4]
Impacts, benefits
Description of environmental benefits
- Heat and cold storage (TES) is used to store heat from the house in the groundwater in the summer. In winter, the energy is used again to heat homes or other buildings. With this technology, an optimal indoor climate in the home or office can be created in summer and winter, without using fossil sources (ref. 4)
- Heat and cold storage stimulates and accelerates biological soil remediation (ref. 4)
- The system is like a washing machine: the water moves back and forth in the pipes that go into the ground. The microorganisms that "eat" the contamination therefore attach themselves to the dirty soil particles, according to laboratory tests, and can thus absorb extra pollution. The organisms also search for the warm well where they multiply much faster. "It is a self-reinforcing process whereby the bacteria absorb up to a factor of ten more pollution and make it harmless (ref. 4)
- “The combination of TES and biological groundwater cleaning is, therefore, a sustainable marriage between sustainable energy production and groundwater cleaning (ref. 4)
- Utrecht, one of the signatories of the climate agreement between Municipalities and Central Government, as a Millennium Municipality aims to be energy neutral by 2030. Energy neutral also means that the "municipal" CO2 production is compensated (offset) by purchasing and generating sustainable energy (ref. 5)
Description of economic benefits
Expected that impact in terms of cost reduction is 89 million euros because traditional soil decontamination procedures would have cost around 100 million euros and with the Bio Washing Machine this costs about 11 million euros (ref. 3)
Social and cultural impacts
Description of social and cultural benefits
Unknown
Type of reported impacts
Indicators
Climate action: saved 6.000 tonnes of CO2/year (ref. 10)
Regarding soil decontamination: 40% reduction of volatile organic compounds (VOC) mass, which are the decontaminating substances in the soil (ref. 10)
Results indicate that 500kg of VOC has been reduced in 2 years time (ref. 10)
Expected that impact in terms of cost reduction is 89 million euros because traditional soil decontamination procedures would have cost around 100 million euros and with the Bio Washing Machine this costs about 11 million euros (ref. 3)
Analysis of specific impact categories
Job creation: The NBS created ...
Negative impacts: Did the project cause any problems or concerns?
No information was found regarding negative impacts of the project
COVID-19 pandemic
Unknown as of 26 July 2020.
Methods of impact monitoring
Evidence for use of assessment
Presence of an assessment, evaluation and/or monitoring process
Yes
Presence of indicators used in reporting
Yes
Presence of monitoring/evaluation reports
Yes
Availability of a web-based monitoring tool
No evidence in public records
Impact assessment mechanism
Name of any specific impact assessment tools
Assessment indicators are Influx and biodegration capacity. The monitoring tool used is ADAPT [9] which is a tool to monitor urban climate change resiliency.
Another assessment tool used is isotope analysis to assess contamination concentration change [1]
Use of GIS in mapping impacts
No evidence in public records
Citizen involvement
Citizens involvement in assessment/evaluation
Unknown
Citizens involvement in the analysis of the assessment/evaluation
Unknown
Follow-up to the evaluation / assessment
Unknown
References
List of references
1. Rijkswaterstaat. (n.d.). Pilot project 7: Aquifer Thermal Energy Storage. Available at: http://rwsenvironment.eu/subjects/soil/projects/citychlor/pilot-project-7/ (Accessed 26 July 2020)
2. Biowasmachine Stationsgebied Utrecht. (2011). [video] Utrecht: CU 2030. Available at: https://www.youtube.com/watch?v=y8BY4hVYmEk (Accessed 26 July 2020)
3. Biowasmachine – Innovatie gemeente Utrecht. (2014). Utrecht: CU 2030. Available at: https://www.youtube.com/watch?v=m3NEFoDpUrA (Accessed 26 July 2020)
4. Grotenhuis, T. (2015). Snellere grondwaterreiniging door warmte-koudeopslag. [online] Available at: http://www.wur.nl/nl/show/Snellere-grondwaterreiniging-door-warmtekoudeopslag.htm (Accessed 26 July 2020)
5. De Vries, A. (2016). Utrecht – Een biowasmachine in het Stationsgebied. [online]. Available at: http://www.grondwatercollectief.nl/utrecht-een-biowasmachine-in-het-stationsgebied/ (Accessed 26 July 2020)
6. Rijkswaterstaat. (n.d.) City Chlor. [online]. Available at: http://rwsenvironment.eu/subjects/soil/projects/citychlor/ (Accessed 26 July 2020)
7. Gemeente Utrecht. (2016). Grondwater. [online] Available at: https://www.utrecht.nl/wonen-en-leven/duurzame-stad/wateroverlast-voorkomen/grondwater/ (Accessed 26 July 2020)
8. Gemeente Utrecht. (2015). Grondwaterkwaliteit. [online] Available at: https://ckan.dataplatform.nl/dataset/grondwaterkwaliteit (Accessed 26 July 2020)
9. De Vries, A. (2013). “Bio-washing machine and Bioprocess monitoring”. Utrecht: City of Utrecht. [pdf]. Available at:
http://rwsenvironment.eu/publish/pages/109859/20130517_02_albert_de_vries_the_area-oriented_approach_in_the_utrecht_station_area.pdf (Accessed 26 July 2020)
10. De Vries, A. (2013). Case study: Area-oriented approach & the urban development in Station area of Utrecht. Utrecht: City of Utrecht [pdf]. Available at: http://rwsenvironment.eu/publish/pages/109859/20130517_02_albert_de_vries_the_area-oriented_approach_in_the_utrecht_station_area.pdf (Accessed 26 July 2020)
11. City of Utrecht. (2009). "Het Utrechtse Stationsgebied geeft duurzame energie”. Utrecht: City of Utrecht. [pdf] available at https://www.cu2030.nl/images/oud/CONT/C/catalogus_duurzaam_stationsgebied_utrecht.pdf (Accessed 26 July 2020)
12. Gemeente Utrecht. (2015). Gebiedsplan gebiedsgericht grondwaterbeheer en visie op duurzaam gebruik van de ondergrond. [pdf] Available at https://omgevingsvisie.utrecht.nl/fileadmin/uploads/documenten/zz-omgevingsvisie/thematisch-beleid/bodem-grondwater-ondergrond/2015-04-hoofdrapport-gebiedsplan-gebiedsgericht-grondwaterbeheer-en-visie-op-duurzaam-gebruik-van-de-ondergrond.pdf (Accessed 26 July 2020)
13. Gemeente Utrecht. (2009). Beschermen, verbeteren en benutten: Naar een gebiedsgerichte aanpak Grondwaterverontreinigingen in de ondergrond van Utrecht. Utrecht: Utrecht Municipality [pdf]. Available at: http://docplayer.nl/40418870-Beschermen-verbeteren-en-benutten-naar-een-gebiedsgerichte-aanpak-grondwaterverontreinigingen-in-de-ondergrond-van-utrecht.html (Accessed 26 July 2020)
14. Gemeente Utrecht (n.d.). Bodemenergie: vergunning of melding [online] Available at: https://www.utrecht.nl/ondernemen/vergunningen-en-regels/ondernemen-en-milieu/bodemenergie-vergunning-of-melding/ (Accessed 26 July 2020)
Comments and notes