WO2014075724A1

WO2014075724A1 - Unit and method for optical non-contact oil detection

Info

Publication number: WO2014075724A1
Application number: PCT/EP2012/072665
Authority: WO
Inventors: Sergey Babichenko
Original assignee: Nemor Technologies Oü
Priority date: 2012-11-15
Filing date: 2012-11-15
Publication date: 2014-05-22
Also published as: US9863887B2; EP2920576C0; EP2920576A1; US20150293032A1; EP2920576B1

Abstract

The invention relates to a unit and method for detection of presence of oil on the water surface or in the water column. Unit comprises a sensor (2), whereby the sensor is connected to electronic compartment followed by microprocessor controller (4) with embedded software for carrying out necessary analyses of reflected signals received by the sensor (2). The microprocessor controller (4) is connected to communication means (5) for transmitting an alarm signal through external communication line (6) in case of oil pollution. All elements mentioned above are supplied by external power supply (7) and are accommodated into a waterproof housing (8). The sensor comprises the probe light source formed by a pulsed UV LED (10), collimating optics (10') and narrow band optical filter (20), at least one dichroic mirror (30), a projection-receiving lens (40), at least one optical filter (50), at least one photodetector (60) and a reference photodetector (70).

Description

UNIT AND METHOD FOR OPTICAL NON-CONTACT OIL DETECTION

Technical Field

The present invention relates to a unit and method for detection of presence of oil on the water surface or in the water column.

Background Art

In-time detection of water pollution by oil remains a relevant task to prevent environmental damage due to the spill and pollution spreading and loss of the product caused by the leak incidents. Among the variety of the techniques used for the task, the most demanded are the ones capable of operating in real-time, unattended, and with minimal maintenance.

The Light Induced Fluorescence (LIF) is well known high sensitive method used for detection of oil in water. It is referred to as an active method due to the use of controlled light source. The selectivity of oil detection with this method is provided due to the fact that at properly selected spectrum of the inducing light the poly-aromatic hydrocarbons (PAH) of oil products produce fluorescence with specific spectral profile. This profile differs from spectral response of other materials to the same inducing light and due to that can be used for oil detection and quantification.

Another feature of the LIF method is that it can be applied remotely without sampling or contacting the water body. This feature in combination with high selectivity, sensitivity and instantaneous detection allows building the sensor based on LIF method operating continuously in non-contact and real-time mode.

LIF method is effectively realized for oil detection by airborne and shipboard LIDAR (Light Detection and Ranging) monitoring systems. These systems provide high sensitivity and spatial resolution down to meter scale and are capable to detect oil on the water surface, submerged oil, and dissolved and emulsified fractions. Being very effective as mobile units, such systems are often too complex and expensive for continuous local on-site monitoring.

The remote (non-contact) mode of oil detection with LIF method is realized by fluorescence LIDARs (Light Detection and Ranging). The invention according to patent document US5096293 “Differential fluorescence LIDAR and associated detection method” to Cecchi Giovanna, Pantani Luca, 1992 discloses the use of fluorescence LIDAR for real-time remote sensing, and in particular for remote sensing of water. The detection method is based on the inducing the emission of fluorescence radiation from a remote target and collecting such emission with following separation into plurality of predetermined spectral channels. Collected spectral signals are processed in a way of calculating the ratio of each channel signal to each other signal thus providing a form of ratios which is compared further with predetermined stored signals corresponding to defined targets or categories of targets. The method is realized by the system comprised the pulsed laser with optical means to direct the laser beam to the object and to collect back scattered radiation; optical channel separator means for separating a backscattered fluorescence signal into predefined number of channels, and signal processing means for forming a plurality of ratio signals and comparing the value of each ratio signal to values stored in a memory.

In the patent document WO2012015332 “Method for remote detection of oil pollution on the surface of water”, to Belov, Mikhail Leonidovich et al, 2012 there is described a method for oil detection by irradiating the surface of the water in the ultraviolet range at the excitation wavelength and recording the intensity of the fluorescent radiation in two narrow spectral ranges with centers at wavelengths λ₁, λ₂. The wavelengths are selected from the condition for the maximum difference between the value of the radiation intensity ratio (for petroleum products) and the value of the radiation intensity ratio (for water). The measured value for the radiation intensity ratio is compared with threshold values.

The above method is based on the assumption that it is possible to define two wavelengths of fluorescence emission of oil with distinct ratio of intensities compared with that of pure water. Such an assumption does not work in case of oil products having the fluorescence in too distinguishing spectral ranges. For example, at the excitation wavelength 308 nm light oil (gasoline) has a max fluorescence at the emission wavelength 380 nm, and heavy oil (ship fuel) has a max fluorescence at the wavelength 520 nm. There is no any pair of wavelengths providing ratio of intensity distinguishing from clean water and equally usable for detection of both mentioned type of oils.

There is an invention defined in patent US7688428 “Non-contact oil spill detection apparatus and method” to Pearlman; Michael D, 2010 describing a non-contact sensor for oil spill detection based on LIF method.

The invention in US7688428 claims the oil detection method based on the anomalous signal return when oil is present compared with the signal when oil is absent. As the invention does not specify any means for taking into account ambient light and minimizing its influence, one can assume that the variation of ambient light due to glint reflection of sun light from the water surface could produce anomalous increase of the signal in the spectral range 320-400 nm and therefore the method will produce false alarm. As the method does not specify the data analysis, one can assume registering the anomalous signals caused by other than oil light reflecting materials on water surface, also possibly producing false alarms.

The sensor of US7688428 is based on the pulsed light source to produce a beam of light having the apex angle 13-15 degrees and spectrally limited to wavelengths between 225 and 300 nm, which is directed to the water; sensor means for detecting fluorescent light filtered in the spectral range between 320 to 400 nm, means for analyzing data and reporting and/or producing a signal or alarm when analyzed data indicates the presence of any significant amount of oil pollutant. The invention in patent US7688428 claims that high power strobed Xe lamp serves as a light source. The sensor is operated vertically above the water at the distance of 3 to 5 m from the surface and at the angle not more than 7 degrees from vertical. The invention also claims the method of oil detection predicated upon differential measurement, i.e. based on the anomalous signal return that will occur when oil is present, as opposed to when there are no hydrocarbons present.

The sensor described in patent US7688428 has the following limitations.
1) Using powerful Xe-lamp as a light source makes the sensor bulky and power consuming, causing principal limitations of the detection distance due to significant beam divergence (light beam has a shape of cone with apex angle 13-15 degrees), increase of the distance will require unreasonable increase of the power consumption.
2) Inclination of the incidence beam of about 7 degree of vertical to detect sufficient amount of fluorescent flux at the detector indicates that the optical axes of the sensing light beam and detection means do not coincide. The signal detection with optical scheme having misaligned optical axes of the light beam and optical axis of receiving means (bi-static optical layout) is exposed to the distance variation. Therefore even if the sensor is adjusted for the distance to water (for example 3-5 m), the change of the distance due to tides, waves or other processes will cause the fluctuations of fluorescence signal thus influencing the reliability of detection.
3) Due to above described reason the sensor cannot operate at the inclination angle more than 10 degrees from vertical. It limits its installation requirements and hampers operation in scanning mode when the inclination angle is varied.
4) The detection limited to the spectral range 320-400 nm does not allow detection of oil products fluorescing at longer wavelengths (Fig. 2).

Disclosure of Invention

The present invention provides a unit for optical non-contact continuous detection of presence of light, medium and heavy oil products on water.

A unit according to present invention includes a sensor, which is connected to electronic compartment followed by microprocessor controller with embedded software for carrying out necessary analyses of returned signals received by the sensor unit. The microprocessor controller is connected to the communication means for transmitting an alarm signal through external communication line in case of oil pollution, whereby all the above elements are supplied by external power supply and accommodated into a waterproof housing.

The sensor comprises the probe light source formed by a pulsed UV LED, collimating optics and narrow band optical filter. The sensor unit also comprises at least one dichroic mirror, a projection-receiving lens, at least one optical filter, at least one photodetector, and a reference photodetector.

The probe light beam generated by UV LED (10) is guided by collimating optics through the narrow band optical filter onto the dichroic mirror, wherein minor part of said probe light beam is passed through said dichroic mirror into the reference photo detector. The reference photo detector registers the intensity signal of probe light beam generated by UV LED. Said dichroic mirror deflects the major part of probe light beam through projection-receiving lens onto the water surface such that said deflected probe light beam is coaxial with the axis of said projection-receiving lens.

The cut off wavelength of the dichroic mirror is selected such that dichroic mirror reflects UV LED light pulses having wavelength in UV spectral region shorter than cut off wavelength of the dichroic mirror. It passes through the return light in the spectral region of longer wavelengths than the cut off wavelength of the dichroic mirror.

Optical filter is a multi band optical filter passing through induced fluorescent flux of light, medium and heavy oil products and suppressing all other spectral components in the return light flux.

The sensor comprises at least one photodetector to register said filtered return light flux.

The sensor may comprise at least two separate photodetectors, whereby each photodetector having its own long pass optical filter. Return light is divided for each of said photodetectors by at least one beam splitter. In such schematics the differential signal of two detectors is due to the returned light flux in the spectral range limited by two cut-off wavelengths of long pass optical filters. This range can be adjusted by selecting proper cut off wavelengths to register induced fluorescence of specified light, medium or heavy oil products.

The sensor may also comprise three separate photodetectors, each photodetector is coupled with the narrow band optical filter. The passing spectral ranges of narrow band optical filters are selected such that first narrow band optical filter coupled with first photodetector passes through induced fluorescence flux in the spectral range for the light oil products. The second narrow band optical filter coupled with second photodetector passes through induced flux in the spectral range for the medium oil products. The third optical filter coupled with third photodetector passes through induced fluorescence flux in the spectral range for the heavy oil products.

The photodetector may consist from an assembly of photodetectors like an array or a matrix, every detector element of N photodetectors is aligned with the optical filter, providing multichannel spectral detection of the fluorescence.

The sensor according to the invention is scannable up to 45 degrees from a vertical position.

The unit according to the invention has a waterproof and hermetic housing filled with neutral gas at overpressure, providing additional safety of exploitation and protecting optical and electronic components from condensed humidity.

The present invention also provides a method for optical non-contact continuous detection of presence of oil products in the water. According to the method of present invention the light beam pulses are generated continuously with the UV LED and guided by the collimating optics through the optical filter onto the dichroic mirror. From the dichroic mirror the light beam pulses are guided through the optics onto the water. Induced light is guided through the optics into the sensor means for registering signals returned from monitored water surface. Part of each said probe light beam pulse generated by the UV LED is passed though said dichroic mirror into the reference photo detector for registering a signal of the intensity of the probe light beam generated by UV LED pulse. Part of each probe light beam pulse generated by the UV LED is deflected coaxially with the axis of the projection-receiving lens by said dichroic mirror through said projection-receiving lens onto the water surface. Synchronously with each probe light beam pulse a return light signal is collected and passed by the same projection-receiving lens through said dichroic mirror onto the means for registering return light signal.

A return light informative signal is obtained by normalizing return light signal using a signal of the intensity of the probe light beam generated by the UV LED pulse. Between consecutive probe light beam pulses generated by the UV LED a background light signal due the ambient light is registered with the help of the sensor means. Said background light signal is subtracted from the return light informative signal in order to obtain a differential signal. The obtained differential signal levels as an accumulated signal per multiple pulses N of UV LED are compared with the predetermined threshold signal level. An alarm signal is generated when predetermined threshold signal level and duration of time interval limit for consecutive warnings is exceeded.

Brief Description of Drawings

The invention is explained in detail below with reference to the drawings, in which:
Fig 1 shows an electro-mechanical block-scheme of the unit according to the present invention;
Fig 2 shows a first version of an optical layout of the sensor indicated by reference number 2 in Fig 1;
Fig 3 shows the fluorescence spectra of light, medium and heavy oil respectively and transparency curves of dichroic and long pass filters;
Fig 4 shows second version of the optical layout of the sensor according to the invention;
Fig 5 shows third version of the optical layout of the sensor according to the invention;
Fig 6 are shown operational positions of the unit inclined from vertical in scanning mode;
Fig 7 shows a flow chart of the method according to the present invention.

Mode(s) for Carrying Out the Invention

The present invention provides the unit and the method for reliable detection of oil products which may appear in the controlled area and they will be described hereinafter in a more detail.

In Fig 1 is shown electro-mechanical block-scheme of the unit. The unit includes opto-electronic unit 2 (hereinafter - “sensor”) that is provided with a protective snoot 1 and connected to electronic compartment 3 (Fig 1). Sensor is followed by microprocessor controller 4 with embedded software for carrying out necessary analyses of reflected signals received by sensor. The controller 4 is connected to communication means 5 for transmitting an alarm signal through external communication line 6 in case of oil pollution. Considered communication means may be any contact or wireless communication line supported by microcontroller, namely LAN, RS485, Radio Link, Wi-Fi, GSM, Bluetooth, or any other custom solution. The waterproof and hermetic housing can be also filled with neutral gas at overpressure, providing additional safety of exploitation and protecting optical and electronic components from condensed humidity.

Microprocessor controller provides instant analysis of collected signals and communication means deliver the observation result, and more specifically – an alarm, when oil pollution is detected. All the above elements of the unit may be supplied from an external power supply 7 and are accommodated into a waterproof housing 8.

Fig 2 shows a first version of an optical layout of the sensor according to the invention. When describing different versions of the sensor the same elements in figures are designated with the same reference numbers.

The sensor according to the invention includes pulsed UV LED 10; collimating optics 10’, narrow band optical filter 20; dichroic mirror 30; projection-receiving lens 40; optical filter 50; photodetector 60 and reference photodetector 70.

The sensor according to the invention operates as follows. At first the LED 1 (Fig. 2) is switched ON and it emits a pulse of light in UV spectral range with duration τo, and this pulse is collimated with corresponding optical system 10’, 20 and directed to the water surface through dichroic mirror 30 and the lens 40. The long-pass dichroic mirror 30 serves to reflect the LED emission at the wavelength λ_LED and to pass the light with the wavelengths longer than λ_cut through the filter (at the condition that λ_LED < λ_cut). The mirror 30 is used also to align the LED beam to be coaxial with the optical axis of receiving lens 40. Then the UV LED pulse hits the water and induces the fluorescence of constituents in it.

The light flux returned from the water contains scattered light at the wavelength λ_LED and induced fluorescence in the spectral range λ_fl > λ_cut. The lens 40 serves to shape the fluorescence flux within preset divergence to provide optimal cut–off performance of the filter set 50. The fluorescence is collected by the receiving lens 40 and spectrally filtered by the dichroic mirror 30. The cut off wavelength λ_cut is selected such that the fluorescence of oil products passes through the mirror 30. The long pass filter 5 is used to select the fluorescence flux caused by oil products in specific spectral ranges and to suppress all other spectral components in the return light flux.

For example, when the incident fluorescence flux has a divergence lower than 3 degrees, the filter will pass less than 1% of light below cut-off wavelength and 90% with longer wavelengths. At higher divergence the filter will pass 10% of light below cut-off wavelength thus mixing the fluorescence flux with excitation light at the detector 6.

The filtered fluorescence flux is registered by the photo-detector 60 by integrating the return signal in a time interval τ₁ synchronously with the LED pulse (at the condition that τ₁ ≥ τ₀).

Next the LED is switched off and the photo-detector 60 registers the background signal due to the ambient light by integrating such light collected by the lens 40 and passed through the mirror 30 and long pass filter 50 during the same time interval τ₁. Further subtraction of the background signal from the signal of induced fluorescence eliminates the influence of ambient light to the sensor operation for oil detection.

This two-step measuring procedure is repeated N times (N ≥ 1) to produce resulting fluorescence value with subtracted background due to ambient light as an accumulated signal per N pulses of LED. The procedure of signal accumulation serves to increase the SNR at the photodetector 60.

The reference detector 70 is used to register the energy of LED pulse and to normalize the return signal by its value to eliminate any variations of detected fluorescence flux caused by fluctuations of LED intensity in time due to environmental factors, work resource, etc.

The alarm of oil detection is done by the microprocessor controller 4 (Fig 1) which compares the intensity of the accumulated signal with the pre-defined threshold value based on the signal of clean water registered according to the two-step procedure described above. The alarm is reported through the external communication line 6 (Fig 1).

There are several possible configurations of the detection part of the sensor. In the first option the filter 50 could be of multi band design to pass the fluorescence flux to the detector 60 in several specific spectral ranges. For example in such layout one spectral band can be selected to pass the fluorescence flux of light oil products, the next one – for medium oils, and another one – for heavy oil products.

In Fig 3 a fluorescence spectra of light (1), medium (2) and heavy (3) oil in water at the excitation wavelength 350 nm are shown. Transparency curve of dichroic filter is indicated by reference number 4 and transparency curve of dual long pass filter is indicated by reference number 5, respectively.

In this case any type of oil product will give the signal to the detector non-selective towards different oil types. The fluorescence outside of the spectral ranges will be not taken into account, thus minimizing the false alarm rate.

In Fig 4 there is shown more complex optical layout of the sensor, whereby reference number 10 designates pulsed UV LED, 10’ – collimating optics, 20 – narrow band optical filter, 30 - dichroic mirror, 40 – projection-receiving lens, 50 – long pass optical filter, 60 – photodetector, 70 – reference photodetector, 80 - beam splitter for the second detection channel, 80’ – optical beam splitter for one more detection channels, 90, 90’ – different optical filters, and 100, 100’ – photodetectors, respectively.

In this layout of the detection part of the sensor unit the fluorescence flux collected by the lens 40 is split into several beams (channels) by the beam splitter 80, 80’ positioned along the optical axis of the lens 40, everyone of which is followed by detector assembly consisting of photo-detector 60 coupled with narrow band filter 50. Such detection scheme allows detection of spectral signals in different spectral ranges by a separate detector, thus providing selective information of the spectral range generating the alarm, thus providing better differentiation of the signals due to oil from other materials.

In Fig 5 there is shown yet another optical layout of the sensor, whereby reference number 10 designates pulsed UV LED, 10’ - collimating optics, 20 - optical filter, 30 - dichroic mirror, 4 - receiving lens, 5 - assembly of optical filters, 6 - assembly of photodetectors and 7 - reference photodetector, respectively.

The detector can also consist of the assembly of photo-detectors 60 like an array or a matrix of narrow band spectral filters 50 in front of every detector element of N photodetectors aligned with the set of optical filters 50. Such an assembly is aligned with the optical lens 40 and, when exposed to the fluorescence flux, will provide multichannel spectral detection of the fluorescence. In this scheme even more detail spectral information for differentiation of oil signal from other materials can be obtained. This kind of selective spectral information of the fluorescence signal minimizes the false alarm rate.

The use of pulsed UV LED as a sensing light source delivers a number of benefits. Due to its small size (almost a point light source) it is possible to design a compact optical scheme with minimal losses of the energy at signal detection. Besides that the sensing beam has low divergence providing longer sensing distance at lower power consumption comparing with other light sources. As described above, the pulsed mode of light source operation synchronized with the detector is important in eliminating the influence of the ambient light to the detector. Due to high pulse repetition rate (PRR) of LED (up to 1 kHz) it is possible to realize data sampling and background subtraction accumulated per number of LED pulses (accumulation mode) to improve SNR at the detector.

While the LED light has narrow spectral width, the filter 2 (Fig 5) serves to make the excitation monochromatic in order to provide better separation of excitation light and fluorescence flux.

By using dichroic mirror it is possible to realize compact coaxial design of the sensor. Due to aligned optical axes of the sensing beam and the optical lens 4 the sensor operation does not depend on the inclination angle from vertical position. It is particularly important for on-shore and on buoy installations to monitor adjacent water surfaces. This feature is of principal importance for providing sensing of water with scanning the light beam as indicated in Fig 6. The unit is scannable up to 45 degrees from the vertical position.

The LED with several emission wavelengths can be used in the layouts shown in Fig 5 and 6. When the emission wavelength is controlled, separate detection channels serve to register the fluorescence at different excitation wavelengths, thus providing even better differentiation of oil fluorescence from any other signals.

Synchronous with LED high frequency data sampling by the detector gives the possibility to differentiate the short-term and long-term variations of the signal at the detector, providing additional information for decision making and increasing the reliability of alarm generation. Using a solid state detector in combination with LED allows low voltage sensor operation, and it reduces the risk in its application in highly explosive fire-hazardous environments (e.g. oil terminals, pipelines, off-shore platforms).

Low power consumption makes possible long-time sensor operation with storage or solar batteries. This feature is of great importance for sensors installed for autonomous operations without power lines available.

The method of oil detection according to present invention is based on the registration of the integral intensity of fluorescence emission in the spectral ranges defined by detector configuration and recorded as an accumulated difference of the intensity I ₁ of the return light flux during the LED pulse and without it (i.e. I ₂).

In this way the background signal due to ambient light is not taken into account. When the accumulated signal exceeds the pre-defined threshold I ₀ (i.e. (<I ₂ - I ₁ >) > <I ₀ >), the microcontroller produces the alarm signal. The threshold may be defined as an averaged intensity of the sensor signal over M pulses of LED recorded from the clean water after sensor installation on-site.

The flow chart of the method of oil detection is shown in Fig. 7. The process starts with measuring the ambient light flux in the preselected spectral range(s) Δλ defined by the configuration of filter sets 5, 9 and 9’ in Fig. 2, 4 and 5. The background signal I ₁ on the detector is integrated during time interval τ₁. The latter is defined by the duration of the LED light pulse by the condition τ₁ > τ₀. Then the LED pulse is generated. The detector records the return light signal I’ ₂ synchronously with the LED light pulse in the same preselected spectral range(s) Δλ during the same time interval τ₁. Simultaneously the reference detector records the signal I _r proportional to light flux of LED. Then the signal I’ ₂ is normalized by I _r and the informative signal I ₂ is produced. After that the background signal I ₁ is subtracted from informative signal I ₂ resulting in the differential signal I _d =I ₂ -I ₁. The differential signal is accumulated during the cycle of preset number of LED pulses N: I = Σ I _d /N. If accumulated signal I exceeds the threshold I ₀ the system sets the warning status. The threshold signal I ₀ is defined by described measuring procedure when the water surface is supposed to be in normal conditions (clean), e.g. after on-site installation of the sensor. The time of continuous warning status is counted by the system, and when its duration exceeds the threshold T₀, the system reports an alarm.

The time T₀ is defined by application requirements. By taking into account the sizes of oil patches and the flow velocity in the controlled area, it is possible to set-up the reasonable “alarm generation time”. For example, if the oil patch of 1 m size is considered as noticeable, and the flow velocity in the area is 0.5 m per second, then such patch will remain in the field of view of the sensor during 2 seconds. In this time frame the sensor operating at the sampling rate 10Hz will provide 20 continuous warning signals providing statistical confirmation for reporting alarm. Such analysis of detected signals with optimized PRR, accumulation time and alarm generation time according to on-site conditions lowers the risk of false alarms by filtering off single instantaneous variations exceeding the threshold for warning.

The accumulation of signal per N pulses of LED usually provides SNR increase by root of number N. For example signal accumulation per 100 LED pulses at the pulse frequency 100 Hz will increase SNR by order of magnitude in 1 sec time interval. From one hand such time is reasonably short and allows detection of small oil patches even in water with strong current. From the other hand, analysis of 100 signals recorded inside accumulation time allows excluding the short time spikes of the signal caused by other reasons or objects. Such analysis of detected signals with optimized PRR and accumulation time according to on-site conditions lowers the risk of false alarm by filtering off single instantaneous variations exceeding the threshold.

In case of multichannel detection specified in Fig 4 and 5 the flow chart according to Fig 7 is equally performed for every single detection channel synchronously with the LED pulse. As a result, the threshold signal I0 is defined individually for every detection channel, and exceeding such threshold provides selective information of the spectral range generating the alarm, thus better differentiating the signals due to oil from other materials.

When the detection configuration with several channels is used, the method of data analysis compares the difference in signals in defined spectral channels influenced by oil products with the corresponding values of the signal in other detection channels influenced by other organic materials in water to distinguish oil product appearance in the waters with variable organic content (i.e. run-off, waste or other industrial waters). This increases the reliability of oil detection.

The invention is not limited to the embodiments described above and there may be made various changes and modifications not deviating from the scope of appended claims.

Claims

Unit for optical non-contact continuous detection of presence of light, medium and heavy oil products on water, according to present invention includes a sensor (2), whereby the sensor is connected to electronic compartment followed by microprocessor controller (4) with embedded software for carrying out necessary analyses of reflected signals received by the sensor (2), the microprocessor controller (4) is connected to communication means (5) for transmitting an alarm signal through external communication line (6) in case of oil pollution, whereby all the above elements are supplied by external power supply (7) and accommodated into a waterproof housing (8), characterized in that said sensor comprises the probe light source formed by a pulsed UV LED (10), collimating optics (10’) and narrow band optical filter (20), at least one dichroic mirror (30), a projection-receiving lens (40), at least one optical filter (50), at least one photodetector (60), and a reference photodetector (70).
Unit according to claim 1, characterized in that the probe light beam generated by UV LED (10) pulse is guided by collimating optics (10’) through the narrow band optical filter (20) onto the dichroic mirror (30), wherein one part of said probe light beam is passed through said dichroic mirror (30) into the reference photo detector (70) for registering the intensity signal (I _r) of probe light beam generated by UV LED (10), said dichroic mirror (30) deflects the major part of probe light beam through projection-receiving lens (40) onto the water surface such that said deflected probe light beam is coaxial with the axis of said projection-receiving lens (40).
Unit according to claim 1, characterized in that the cut off wavelength (λCUT) of the dichroic mirror (30) is selected such that dichroic mirror (30) reflects UV LED light pulses having wavelength (λ_LED) in UV spectral region shorter that cut off wavelength (λ_CUT) of the dichroic mirror and passes through the return light in the spectral region of longer wavelengths than the cut off wavelength (λ_CUT) of the dichroic mirror.
Unit according to claim 1, characterized in that the optical filter (50) is a multi band long pass optical filter passing through induced fluorescent flux of light, medium and heavy oil products and suppressing all other spectral components in the return light flux.
Unit according to claim 1, characterized in that the sensor comprises at least two separate photodetectors (60), each photodetector (60) having its own long pass optical filter (50), wherein return light is divided for each of said corresponding photodetectors by at least one beam splitter (80).
Unit according to claim 1, characterized in that sensor unit comprises three separate photodetectors (60), each photodetector is coupled with the narrow band optical filter (50), the passing spectral ranges of narrow band optical filters are selected such that one narrow band optical filter coupled with first photodetector passes through induced fluorescence flux in the spectral range for the light oil products, the second narrow band optical filter coupled with second photodetector passes through induced flux in the spectral range for the medium oil products and third optical filter coupled with third photodetector passes through induced fluorescence flux in the spectral range for the heavy oil products.
Unit according to claim 1, characterized in that the photodetector (60) consists from an assembly of (N) photodetector elements like an array or a matrix, every photodetector element is aligned with the optical filter (50), providing multichannel spectral detection of the fluorescence.
Unit according to claim 1, characterized in that the unit (8) is scannable up to 45 degrees from the vertical position.
Unit according to claim 1, characterized in that the waterproof housing (8) of the unit is filled with gas at overpressure, providing additional safety of exploitation.
Unit according to claim 1, characterized in that the UV LED (10) of the unit emits light at single wavelength or at multiple wavelengths in controlled mode.
Method for optical non-contact continuous detection of presence of oil products on the water, according to which method probe light beam pulses are generated and guided through the optics onto the water and the reflected from the water surface return light is guided through the optics into the sensor unit for registering signals, characterized by the following steps:

the ambient light flux in the preselected spectral range(s) Δλ is integrated by photodetector (60) during time interval τ₁ and the background signal I ₁ is obtained, whereby interval τ₁ is defined by the duration UV LED light pulse τ₀ by the condition τ₁ > τ₀;

a preset number (N) of probe light beam pulses with duration τ₀ are generated continuously with the UV LED (10) and guided by the collimating optics (10’) through the optical filter (20) onto the dichroic mirror (30);

part of each of said probe light beam pulse generated by the UV LED (10) is passed through said dichroic mirror (30) into the reference photo detector (70) for registering a signal (I _r) proportional to the intensity of the probe light flux generated by UV LED (10) pulse;

major part of each probe light beam pulse generated by the UV LED (10) is deflected coaxially with the axis of the projection-receiving lens (40) by said dichroic mirror (30) through said projection-receiving lens (40) onto the water surface;

synchronously with each probe light beam pulse a return light signal (I’ ₂) is collected and passed by the same projection-receiving lens (40) through said dichroic mirror (30) onto the detector means (50, 60) for registering the return light signal (I’ ₂);

a return light informative signal (I ₂) is produced by normalizing return light signal (I’ ₂) using a reference signal (I _r) of reference photodetector, background light signal (I ₁) is subtracted from the return light informative signal (I ₂) in order to obtain differential signal (I _d).
Method according to claim 11, characterized in that the obtained and accumulated during (N) cycles differential signal (I _d) levels are accumulated as a signal (I) and compared with the predetermined threshold signal (I ₀) level, and when signal (I) exceeds threshold signal (I ₀) level, a warning is set.
Method according to claim 12, characterized in that when the counted time interval (T) of consequent warnings exceeds the preset time interval T₀ set for consequent warning status, the alarm signal is generated.