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PILOT SCALE DEMONSTRATION PROJECT LIFE Stop CyanoBloom SOLUTION FOR IN-LAKE DETECTION AND GROWTH CONTROL OF CYANOBACTERIA A rapid cyanobacterial bloom collapse with the release of toxic substances into the water environment and consequently diminished water quality status is the most unwanted consequence of eutrophic water conditions. Although a lot has been done in some places to provide catchment preventive measures against eutrophication, additional efforts are still needed to predict and prevent cyanobacterial bloom. For this purpose, an accurate real-time information on the spatiotemporal distribution of cyanobacterial bloom is vital. Only such information can enable targeted cyanobacterial control, avoiding treatment of entire water volumes. We can obtain such a three-dimensional localisation of cyanobacteria and information on their physiological status by exploiting their auto-fluorescence. Also, electrochemical oxidation with hydroxyl radicals produced from water in electrolytic cell proved to be efficient in halting cyanobacterial proliferation, as well as microcystin degradation [1]. In the LIFE Stop CyanoBloom project, we have integrated the approach into a robotic vessel enabling cyanobacterial detection in different depths, localised treatment and immediate detection of provoked effects, as well as automatic collecting of samples for further laboratory analysis. Tinkara Rozina 1 , Maja Zupančič Justin 1 , Domen Leštan 2 , Bojan Sedmak 3 1 Arhel d.o.o. and Envit d.o.o., Ljubljana, Slovenia 2 Biotechnical Faculty, University of Ljubljana, Slovenia 3 National Institute of Biology, Ljubljana, Slovenia Contact information: Arhel d.o.o. Pustovrhova 15 1210 Ljubljana - Šentvid, Slovenia EU E-mail: [email protected] CONCLUSIONS The treatment of Microcystis aeruginosa toxic strain with the electrolytic cell resulted in a complete inhibition of proliferation. The concentration of extracellular toxins of the treated sample did not exceed the concentration of extracellular toxins of the control sample. Products of the Microcystis aeruginosa treatment with bdd electrodes affect the growth of Pseudokirchneriella subcapitata similarly or less than in the case of negative control, which are Microcystis aeroginosa cells treated with ultrasound. INNOVATIVE TECHNOLOGY FOR CYANOBACTERIAL BLOOM CONTROL DEVELOPMENT OF ROBOTIC VESSEL AND DEMONSTRATION OF ITS OPERATION INTEGRATED REAL-TIME INFORMATION ON THE SPATIOTEMPORAL DISTRIBUTION OF CYANOBACTERIAL OCCURRENCE AND TARGETED CYANOBACTERIAL GROWTH CONTROL A NEWLY DEVELOPED EQUIPMENT WITHIN LIFE+ PROJECT WITH INNOVATIVE SOLUTIONS Specially developed hardware within the project allows the robotic vessel the abstraction of water from different depths for measurements of water parameters, the decision on turning on the electrolytic cell to prevent further growth of cyanobacteria, or to abstract water samples for further laboratory analysis. All the systems on board are interconnected and communicate via an RS485 network. An additional component is an information system that allows remote navigation of the vessel, transfer, storage, processing and graphical display of obtained data. WATER FLOW REGULATION WITH SMART VALVES (5) The water flow system in the vessel and the automatic sampler are equipped with smart valves. Valve`s drive motor and integrated electronics allow for automatic control and integration of the valves into a larger system with the synchronised operation. Flow regulation is carried out with a stepwise compression of the hose, which is inserted into the valve. The design of the valve allows for easy replacement of the hose (e.g. to prevent contamination of the sample), the use of hoses of different diameters, and mechanical properties. The valve controls the flow directly by the consumption of electric power. This provides reliable operation of the valve with no need for additional sensors or switches. AUTOMATIC WATER SAMPLER (4) WITH A WINCH (3) The sampler enables abstraction of six 1 litre water samples from different depths using a winch with a hose. The command for the sample abstraction is transmitted via RS485 network (in the vessel), via PC through USB connection, or by pressing the button on the control console (when used as an autonomous device). Innovative smart valves allow abstraction of samples without contamination with the water already taken. Sampler`s electronics allows automatic collection of samples at the programmed time, detection of possible failures (leaking containers, pump failure, clogged pipe) and avoidance of spills with automatic shut-off. WATER QUALITY FLOW-THROUGH MEASURING CHAMBER (1) Newly designed water quality flow-through measuring chamber allows online measuring of water quality parameters on board by pumping the water from different depths. It enables simultaneous reading from five sensors (e.g. phycocyanin, chlorophyll, temperature, oxygen, conductivity, pH). Submersible chlorophyll and phycocyanin fluorescence sensors with the automatic cleansing system are used for cyanobacteria and algae quantification. A magnetic stirrer is incorporated into the bottom of the chamber to prevent settling of the phytoplankton. Signals are transferred to a printed circuit inside of an electronics enclosure, where they are converted to a digital form and transferred to a PC for further data analysis. ELECTROLYTIC CELL (2) FOR PREVENTION OF CYANOBACTERIA PROLIFERATION AND DEGRADATION OF CYANOTOXINS A single-compartment electrolytic cell equipped with boron-doped diamond (BDD) electrodes is used for electrochemical stimulation of detected cyanobacterial directly in water. Water is pumped through the cell equipped inside with small flow deflectors to achieve laminar flow. Within the cell, short-lived hydroxyl radicals (•OH) are produced directly from water with the use of electric power. The BDD electrodes are advanced inert electrodes with the highest potential of •OH production achieving inhibition and degradation of cyanotoxins, suppression of further cyanobacterial proliferation or their lysis, depending on the electrolysis length and current density applied. INFORMATION SYSTEM FOR TRANSFER AND PRESENTATION OF MEASURED DATA The integrated information system allows three-dimensional inventory of the status of a water body. With all its sensors, the vessel reports to the operator its GPS location, depth, the presence of algae and cyanobacteria, water temperature, electrical conductivity, dissolved oxygen and pH. The vessel reports real-time data via GSM communication to the user, providing an accurate picture of the current state of the water body, which can be displayed by a web browser. GSM module sends the data also to the TCP / IP server, which can be located at a remote location of the operator, where the data are stored in MySQL database. The user-friendly data processing software enables analysis and graphical representation of the stored data adapted to the geographical picture of the water body. AUTOMATIC DOCKING The vessel is navigated manually, or a route plan is set by a PC. After a completed mission, the vessel returns to its home position and the automatic docking starts. With the use of a compass and a robot vision, the vessel determines its precise position relative to the docking station. When the position is known, robot vision and measured values of obstacle detection sensors are used as input variables of a fuzzy logic controller, which adjusts the vessel's heading and speed accordingly to enter the dock safely. REDUCTION OF CELL AND MICROCYSTIN CONCENTRATION AFTER ELECTROCHEMICAL OXIDATION ACKNOWLEDGMENTS The work was performed in the frame of LIFE12ENV/SI/783 and Research Project L1-5456. The authors thank LIFE Stop CyanoBloom engineering and research group: Gorazd Lakovič, Mario Marinović, Luka Teslić, Jošt Grum, Maša Čater, Tina Eleršek, Andrey Yakuntsov, Branko Hamiti, Tomaž Varlec, Neža Finžgar leaded by Marko Gerl for designing and manufacturing of all the equipment presented in the paper and the research support. REFERENCES [1] Meglič, A. et al., Electrochemical inactivation of cyanobacteria and microcystin degradation using a boron-doped diamond anode – A potential tool for cyanobacterial bloom control. J. Environ. Sci. (2016), http ://dx.doi.org/10.1016/j.jes.2016.02.016 0,00E+00 1,00E+06 2,00E+06 3,00E+06 4,00E+06 5,00E+06 6,00E+06 7,00E+06 0 24 48 72 Concentration [cells/mL] Time [hours] The figures represent the effects of electrochemical oxidation on laboratory-grown toxic cyanobacterial culture Microcystis aeruginosa PCC 7806 with initial concentration 5∙10 6 cells/ml, 72 hours after a single treatment using BDD electrodes with a current density 10 mA/cm 2 and 75 mL/min flow-rate. While cell concentration and total cyanotoxins exhibited steady growth all 72 hours after the start of the observation in the control sample, the treated sample exhibited a reduction of cells and concentration of total cyanotoxins. 0 100 200 300 400 500 600 0 24 48 72 Total microcystin concentration [ng/mL] Time [hours] Control BDD treatment Direction of water flow through key elements of the vessel: measuring chamber, electrolytic cell and automatic sampler. 1 Measuring chamber 5 Smart valve 2 Electrolytic cell 3 Winch with a hose 4 Automatic sampler Wind meter, data transfer mechanism, compass, camera Front camera Photovoltaic panel, batteries Lifting electric propulsion system Presented at
Transcript

PILOT SCALE DEMONSTRATION PROJECT LIFE Stop CyanoBloom

SOLUTION FOR IN-LAKE DETECTION AND GROWTH CONTROL OF CYANOBACTERIA A rapid cyanobacterial bloom collapse with the release of toxic substances into the water environment and consequentlydiminished water quality status is the most unwanted consequence of eutrophic water conditions. Although a lot hasbeen done in some places to provide catchment preventive measures against eutrophication, additional efforts are stillneeded to predict and prevent cyanobacterial bloom. For this purpose, an accurate real-time information on thespatiotemporal distribution of cyanobacterial bloom is vital. Only such information can enable targeted cyanobacterialcontrol, avoiding treatment of entire water volumes. We can obtain such a three-dimensional localisation ofcyanobacteria and information on their physiological status by exploiting their auto-fluorescence. Also, electrochemicaloxidation with hydroxyl radicals produced from water in electrolytic cell proved to be efficient in halting cyanobacterialproliferation, as well as microcystin degradation [1].In the LIFE Stop CyanoBloom project, we have integrated the approach into a robotic vessel enabling cyanobacterialdetection in different depths, localised treatment and immediate detection of provoked effects, as well as automaticcollecting of samples for further laboratory analysis.

Tinkara Rozina1, Maja Zupančič Justin1, Domen Leštan2, Bojan Sedmak3

1Arhel d.o.o. and Envit d.o.o., Ljubljana, Slovenia2Biotechnical Faculty, University of Ljubljana, Slovenia

3 National Institute of Biology, Ljubljana, Slovenia

Contact information:Arhel d.o.o. Pustovrhova 15

1210 Ljubljana - Šentvid, Slovenia EUE-mail: [email protected]

CONCLUSIONS

• The treatment of Microcystis aeruginosa toxic strain with the electrolytic cell resulted in a complete inhibition of proliferation.

• The concentration of extracellular toxins of the treated sample did not exceed the concentration of extracellular toxins of the control sample.

• Products of the Microcystis aeruginosa treatment with bdd electrodes affect the growth of Pseudokirchneriella subcapitata similarly or less than in the case of negative control, which are Microcystis aeroginosa cells treated with ultrasound.

INNOVATIVE TECHNOLOGY FOR CYANOBACTERIAL BLOOM CONTROLDEVELOPMENT OF ROBOTIC VESSEL AND DEMONSTRATION OF ITS OPERATION

INTEGRATED REAL-TIME INFORMATION ON THE SPATIOTEMPORAL DISTRIBUTION OF CYANOBACTERIAL OCCURRENCEAND TARGETED CYANOBACTERIAL GROWTH CONTROL

A NEWLY DEVELOPED EQUIPMENT WITHIN LIFE+ PROJECTWITH INNOVATIVE SOLUTIONSSpecially developed hardware within the project allows the robotic vessel the abstraction of water from different depthsfor measurements of water parameters, the decision on turning on the electrolytic cell to prevent further growth ofcyanobacteria, or to abstract water samples for further laboratory analysis. All the systems on board are interconnectedand communicate via an RS485 network. An additional component is an information system that allows remote navigationof the vessel, transfer, storage, processing and graphical display of obtained data.

WATER FLOW REGULATION WITH SMART VALVES (5)The water flow system in the vessel and the automatic sampler are equipped with smart valves. Valve`s drive motor andintegrated electronics allow for automatic control and integration of the valves into a larger system with the synchronisedoperation. Flow regulation is carried out with a stepwise compression of the hose, which is inserted into the valve. Thedesign of the valve allows for easy replacement of the hose (e.g. to prevent contamination of the sample), the use of hosesof different diameters, and mechanical properties. The valve controls the flow directly by the consumption of electricpower. This provides reliable operation of the valve with no need for additional sensors or switches.

AUTOMATIC WATER SAMPLER (4) WITH A WINCH (3)The sampler enables abstraction of six 1 litre water samples from different depths using a winch with a hose. Thecommand for the sample abstraction is transmitted via RS485 network (in the vessel), via PC through USB connection, orby pressing the button on the control console (when used as an autonomous device). Innovative smart valves allowabstraction of samples without contamination with the water already taken. Sampler`s electronics allows automaticcollection of samples at the programmed time, detection of possible failures (leaking containers, pump failure, cloggedpipe) and avoidance of spills with automatic shut-off.

WATER QUALITY FLOW-THROUGH MEASURING CHAMBER (1)Newly designed water quality flow-through measuring chamber allows online measuring of water quality parameters onboard by pumping the water from different depths. It enables simultaneous reading from five sensors (e.g. phycocyanin,chlorophyll, temperature, oxygen, conductivity, pH). Submersible chlorophyll and phycocyanin fluorescence sensors withthe automatic cleansing system are used for cyanobacteria and algae quantification. A magnetic stirrer is incorporatedinto the bottom of the chamber to prevent settling of the phytoplankton. Signals are transferred to a printed circuit insideof an electronics enclosure, where they are converted to a digital form and transferred to a PC for further data analysis.

ELECTROLYTIC CELL (2) FOR PREVENTION OF CYANOBACTERIAPROLIFERATION AND DEGRADATION OF CYANOTOXINSA single-compartment electrolytic cell equipped with boron-doped diamond (BDD) electrodes is used for electrochemicalstimulation of detected cyanobacterial directly in water. Water is pumped through the cell equipped inside with small flowdeflectors to achieve laminar flow. Within the cell, short-lived hydroxyl radicals (•OH) are produced directly from waterwith the use of electric power. The BDD electrodes are advanced inert electrodes with the highest potential of •OHproduction achieving inhibition and degradation of cyanotoxins, suppression of further cyanobacterial proliferation ortheir lysis, depending on the electrolysis length and current density applied.

INFORMATION SYSTEM FOR TRANSFER AND PRESENTATIONOF MEASURED DATAThe integrated information system allows three-dimensional inventory of the status of a water body. With all its sensors,the vessel reports to the operator its GPS location, depth, the presence of algae and cyanobacteria, water temperature,electrical conductivity, dissolved oxygen and pH. The vessel reports real-time data via GSM communication to the user,providing an accurate picture of the current state of the water body, which can be displayed by a web browser. GSMmodule sends the data also to the TCP / IP server, which can be located at a remote location of the operator, where thedata are stored in MySQL database. The user-friendly data processing software enables analysis and graphicalrepresentation of the stored data adapted to the geographical picture of the water body.

AUTOMATIC DOCKINGThe vessel is navigated manually, or a route plan is set by a PC. After a completed mission, the vessel returns to its homeposition and the automatic docking starts. With the use of a compass and a robot vision, the vessel determines its preciseposition relative to the docking station. When the position is known, robot vision and measured values of obstacledetection sensors are used as input variables of a fuzzy logic controller, which adjusts the vessel's heading and speedaccordingly to enter the dock safely.

REDUCTION OF CELL AND MICROCYSTIN CONCENTRATIONAFTER ELECTROCHEMICAL OXIDATION

ACKNOWLEDGMENTS The work was performed in the frame of LIFE12ENV/SI/783 and Research Project L1-5456. Theauthors thank LIFE Stop CyanoBloom engineering and research group: Gorazd Lakovič, Mario Marinović, Luka Teslić, JoštGrum, Maša Čater, Tina Eleršek, Andrey Yakuntsov, Branko Hamiti, Tomaž Varlec, Neža Finžgar leaded by Marko Gerl fordesigning and manufacturing of all the equipment presented in the paper and the research support.

REFERENCES [1] Meglič, A. et al., Electrochemical inactivation ofcyanobacteria and microcystin degradation using a boron-dopeddiamond anode – A potential tool for cyanobacterial bloomcontrol. J. Environ. Sci. (2016),http://dx.doi.org/10.1016/j.jes.2016.02.016

0,00E+00

1,00E+06

2,00E+06

3,00E+06

4,00E+06

5,00E+06

6,00E+06

7,00E+06

0 24 48 72

Co

nce

ntr

atio

n [

cells

/mL]

Time [hours]

The figures represent the effects of electrochemical oxidation on laboratory-grown toxic cyanobacterial cultureMicrocystis aeruginosa PCC 7806 with initial concentration 5∙106 cells/ml, 72 hours after a single treatment using BDDelectrodes with a current density 10 mA/cm2 and 75 mL/min flow-rate. While cell concentration and total cyanotoxinsexhibited steady growth all 72 hours after the start of the observation in the control sample, the treated sample exhibiteda reduction of cells and concentration of total cyanotoxins.

0

100

200

300

400

500

600

0 24 48 72

Tota

l mic

rocy

stin

co

nce

ntr

atio

n [

ng/

mL]

Time [hours]

Control

BDD treatment

Direction of water flow through key elements ofthe vessel: measuring chamber, electrolytic celland automatic sampler.

1 Measuring chamber

5 Smart valve

2 Electrolytic cell

3 Winch with a hose

4 Automatic sampler

Wind meter, data transfer mechanism, compass, camera

Front camera

Photovoltaic panel, batteries

Lifting electric propulsion system

Presented at

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