The Translation of Polder

Author(s):  
Simon Richter

Polder is a Dutch word that occurs in many world languages. As sea level rises and coastal cities subside, the polder is a preferred way to protect land from flooding. Because polder combines infrastructure with governance and social resilience, the translation of polder involves more than finding a linguistic equivalent. Successful translation of polder as both a term and an approach to water management depends on the openness of the translation process to adaptations called for by the local language, culture, climate, and terrain. This chapter begins with cultural histories of the polder in The Netherlands and Indonesia and concludes with close analysis of the translation process as it played out in Water as Leverage for Asian Cities, a Dutch urban design initiative that took place in Semarang, Indonesia in 2018–2019.

Author(s):  
J. A. de Waal ◽  
A. G. Muntendam-Bos ◽  
J. P. A. Roest

Abstract. Reliable prediction of the induced subsidence resulting from gas production is important for a near sea level country like the Netherlands. Without the protection of dunes, dikes and pumping, large parts of the country would be flooded. The predicted sea-level rise from global warming increases the challenge to design proper mitigation measures. Water management problems from gas production induced subsidence can be prevented if measures to counter its adverse effects are taken timely. This requires reliable subsidence predictions, which is a major challenge. Since the 1960's a number of large, multi-decade gas production projects were started in the Netherlands. Extensive, well-documented subsidence prediction and monitoring technologies were applied. Nevertheless predicted subsidence at the end of the Groningen field production period (for the centre of the bowl) went from 100 cm in 1971 to 77 cm in 1973 and then to 30 cm in 1977. In 1984 the prediction went up again to 65 cm, down to 36 cm in 1990 and then via 38 cm (1995) and 42 cm (2005) to 47 cm in 2010 and 49 cm in 2013. Such changes can have large implications for the planning of water management measures. Until 1991, when the first event was registered, production induced seismicity was not observed nor expected for the Groningen field. Thereafter the number of observed events rose from 5 to 10 per year during the 1990's to well over a hundred in 2013. The anticipated maximum likely magnitude rose from an initial value of less than 3.0 to a value of 3.3 in 1993 and then to 3.9 in 2006. The strongest tremor to date occurred near the village of Huizinge in August 2012. It had a magnitude of 3.6, caused significant damage and triggered the regulator into an independent investigation. Late 2012 it became clear that significantly larger magnitudes cannot be excluded and that values up to magnitude 5.0 cannot be ruled out. As a consequence the regulator advised early 2013 to lower Groningen gas production by as much and as fast as realistically possible. Before taking such a decision, the Minister of Economic Affairs requested further studies. The results became available early 2014 and led to the government decision to lower gas production in the earthquake prone central area of the field by 80 % for the next three~years. In addition further investigations and a program to strengthen houses and infrastructure were started. Important lessons have been learned from the studies carried out to date. It is now realised that uncertainties in predicted subsidence and seismicity are much larger than previously recognised. Compaction, subsidence and seismicity are strongly interlinked and relate in a non-linear way to production and pressure drop. The latest studies by the operator suggest that seismic hazard in Groningen is largely determined by tremors with magnitudes between 4.5 and 5.0 even at an annual probability of occurrence of less than 1 %. And that subsidence in 2080 in the centre of the bowl could be anywhere between 50 and 70 cm. Initial evaluations by the regulator indicate similar numbers and suggest that the present seismic risk is comparable to Dutch flooding risks. Different models and parameters can be used to describe the subsidence and seismicity observed so far. The choice of compaction and seismicity models and their parameters has a large impact on the calculated future subsidence (rates), seismic activity and on the predicted response to changes in gas production. In addition there are considerable uncertainties in the ground motions resulting from an earthquake of a given magnitude and in the expected response of buildings and infrastructure. As a result uncertainties in subsidence and seismicity become very large for periods more than three to five years into the future. To counter this a control loop based on interactive modelling, measurements and repeated calibration will be used. Over the coming years, the effect of the production reduction in the centre of the field on subsidence and seismicity will be studied in detail in an effort to improve understanding and thereby reduce prediction uncertainties. First indications are that the reduction has led to a drop in subsidence rate and seismicity within a period of a few months. This suggests that the system can be controlled and regulated. If this is the case, the integrated loop of predicting, monitoring and updating in combination with mitigation measures can be applied to keep subsidence (rate) and induced seismicity within limits. To be able to do so, the operator has extended the field-monitoring network. It now includes PS-InSAR and GPS stations for semi-permanent subsidence monitoring in addition to a traditional network of levelling benchmarks. For the seismic monitoring 60 shallow (200 m) borehole seismometers, 60 + accelerometers and two permanent downhole seismic arrays at reservoir level will be added. Scenario's spanning the range of parameter and model uncertainties will be generated to calculate possible subsidence and seismicity outcomes. The probability of each scenario will be updated over time through confrontation with the measurements as they become available. At regular intervals the subsidence prediction and the seismic risk will be re-evaluated. Further mitigation measures, possibly including further production measures will need to be taken if probabilities indicate unacceptable risks.


2017 ◽  
Vol 14 (3-4) ◽  
pp. 269-293 ◽  
Author(s):  
Lorenzo Squintani ◽  
Ernst Plambeck ◽  
Marleen van Rijswick

The Netherlands has a long and fascinating history of water management. The main features of the Dutch water governance system for the implementation of the wfd are its regional water authorities based on hydrological scales and powers to regulate, decide and raise taxes for their water tasks. Their functional approach and the decentralised character make the regional water authorities very efficient and effective. It is therefore understandable that eu institutions and other Member States consider the Dutch system an interesting potential source of inspiration for other jurisdictions. Yet, it is not all gold what shines. This paper highlights the strength and weakness elements of the Dutch water governance system under the wfd. It exposes several points of concern. When considering using the Dutch experience as a source of inspiration in other Member States, these concerns should be taken in due account.


2019 ◽  
Vol 4 (1) ◽  
pp. 2-14
Author(s):  
HANS BLEUMINK

Historical surface irrigation of pastures in the Dutch province of Noord-Brabant: visible traces of a failed experiment In the second half of the 19th century, some major changes occurred in the water management of the eastern and southern provinces of the Netherlands. Unlike the low-lying western parts of the Netherlands which were characterised by polders and had a long history of formal water boards, the higher eastern and southern parts of the Netherlands were characterized by brook systems and sandy soils, and had no centralised water boards until 1850. From the 1850s onward, water boards were introduced in these higher regions as well, and agronomical scientists and organisations like the Nederlandse Heidemaatschappij endeavoured for the modernisation of agricultural water management. One of their priorities was the introduction of modern forms of surface irrigation of pastures, in order to increase crop yields. In various places modern irrigation systems were constructed. From the 1900s onward, these systems were abandoned due to the introduction of new chemical fertilizers, among others. This article describes the construction and abandonment of one of these modern irrigation systems that was located in Liempde, in the province of Noord-Brabant. The local farmers were not interested in the new technique, and within a few years the system was transformed in a poplar plantation. Nowadays, the area is part of a nature reserve. Nonetheless, the global layout of the irrigation system is still visible.


2018 ◽  
Vol 2 (1) ◽  
Author(s):  
Nikita Kopa-Ovdienko ◽  

To improve the state of the ecosystem of the Haringvliet, an estuary in the Southwest Delta of the Netherlands, the dam, which cuts off the estuary from the sea, will be opened a little in 2018. My research aims to quantify plausible changes of the ecosystem services supply following this water management modification and accompanying habitat restoration measures. For this purpose, values of ecosystem services supply for the relevant ecosystems were collected from the literature and GIS mapping was applied. The study shows clearly that the ecosystem services supply is expected to increase in general following the restoration scenarios. The results can be used for the planning of additional restoration measures aiming to provide the highest possible supply of the ecosystem services.


1983 ◽  
Vol 31 (2) ◽  
pp. 125-135
Author(s):  
C. Bijkerk ◽  
C.G.J. Van Oostrom

Since 1900 seven successive stages can be distinguished in the development of agricultural engineering and in land and water management research in the Netherlands. The development process is traced from the introduction of fertilizers during 1900-1930, through mechanisation, improvement of water management and land accessibility, and increase in the size and specialisation of units, to increasing emphasis on the ecological and recreational value of land. The main features of economical development in agriculture after 1945 are disucssed, including changes in production volume, structure and costs, labour input and productivity, and the cost of wages. The influence of land and water management projects on the rise in agricultural productivity is considered, together with the present policy of selective growth. (Abstract retrieved from CAB Abstracts by CABI’s permission)


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