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How to monitor a large-scale surface-flow constructed wetland with minimal disturbance?

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HAL Id: hal-02334758

https://hal.univ-lorraine.fr/hal-02334758

Submitted on 29 Oct 2019

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How to monitor a large-scale surface-flow constructed

wetland with minimal disturbance?

Marie-Noëlle Pons, N Maurice, Maïa Durozier, Christophe Gauthier, Vincent

Dutreuil, C Pochet, G Jost

To cite this version:

Marie-Noëlle Pons, N Maurice, Maïa Durozier, Christophe Gauthier, Vincent Dutreuil, et al.. How

to monitor a large-scale surface-flow constructed wetland with minimal disturbance?. ILTER-OSM

2019, Sep 2019, Leipzig, Germany. �hal-02334758�

(2)

The AZHUREV surface-flow constructed wetland is a large-scale demonstration wetland built at the outlet of the Grand Reims (France)

wastewater treatment plant (WWTP). Three 20,000 m

2

basins (rectangular shape with different depth distribution within each basin) have been

created: the initial vegetation (mainly P. australis, S. lacustris and G. maxima) density was also different in each basin. Their aim is to polish a part

of the treated wastewater (250 m

3

/h) from the Grand Reims WWTP, as well as to treat part of the Grand Reims stormwater.

M.N. Pons

1,2

, N. Maurice

1

, M. Durozier

1

, C. Gauthier

3

, V. Dutreuil

3

, C. Pochet

4

, G. Jost

5 1

Laboratoire Réactions et Génie des Procédés, Université de Lorraine, CNRS, Nancy, France

2

LTSER-ZA Bassin de la Moselle, Laboratoire Réactions et Génie des Procédés, Université de Lorraine, CNRS, Nancy, France

3 Laboratoire Interdisciplinaire des Environnements Continentaux, Université de Lorraine, CNRS, Nancy & Metz, France

4

Grand Reims, France

5

SINBIO, Muttersholtz, France

Flowmeters have been installed and conductivity/temperature probes have been deployed at the inlet and exit of each basin. The basic

monitoring (chemical variables) of the wetland is routinely done via sampling (monthly basis).

However this does not provide information on the spatial distribution of the pollution in the basins, or of

temperature and dissolved oxygen. Photographs are routinely taken from the shore but, due to the size of the

basins, they do not provide detailed information on the development of the vegetation.

An aquatic drone (Spyboat by CT2MC, Le Bourget-du-Lac, France) which is remotely driven from the shore. It is fitted with a dissolved oxygen probe and a temperature sensor to collect data 10 cm below the surface. It can also collect liquid samples by means of a peristaltic pump. The supersaturation in oxygen observed with the aquatic drone in spring is correlated with the increase of the photosynthetically active solar radiation and the development of algae in the basins. Later in the year, anaerobic zones are detected under the duckweed-covered surface. The aquatic drone is more difficult to operate when the duckweed layer is becoming thick or when the surface is frozen.

Aerial drones are used to better locate dense vegetation beds. However the number of surveys per year is limited (availability, weather conditions)

Grand Reims, June 2018

Liec, June 2019

G. maxima beds Most of the surface is covered by algae and

duckweeds

G. maxima beds have disappeared … Most of the surface is covered by algae and terrestrial plants. On the mission day, free water surface was observed in B1 (30%), B2 (30%) and B3

(15%) (determined by

quantitative image

analysis).

Mavic 2 Pro (DJI)

June 12, 2019 XTC-720P (Secutec) Landsat8 every 16 days 60 pixels Sentinel-2 every ≈ 5 days 134 pixels

DOC and DN gradients observed on Aug. 19th, 2019

D ig gi ng of th e ba si ns Te rr es tr ia l pl an ts St ar t o f op ér at io n St ar t o f op ér at io n Re -s ta rt of op ér at io n

Low color level: free water High green level: plants and algae development

Two satellites are used for remote sensing. Images are usable only in absence

of cloud cover. The

number of pixels is small and only a global analysis of the wetland is possible.

A hunting camera is used for every day monitoring. Only a part of the site can be observed (B3 and the distribution canal). Every day several images are stored by daytime and one MMS is sent.

Final remarks:

All these devices are complementary and are helping us to

monitor remotely (the wetland is 250 km away from the lab) a

large wetland with minimal interference (no walking in the

wetland).

Nancy Reims

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