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Semi-automated penguin counting
 from digital aerial photographs

 S.J McNeill   K Barton     P Lyver       D Pairman


          Landcare Research New Zealand
Motivation
        Understanding changes in penguin population is important,
        as these can be used as indicators of anthropogenic and
        foodweb eects

        Aerial photography is used in the Ross Sea (Antarctica) to
        capture a reliable count of Adélie nesting penguins

        From 1981, the Ross Sea area (158 175
                                                  o    o E) has been

        surveyed annually

        There are many diculties in achieving this census count:
               Timing is critical,
               Ground counting is dicult or impossible,
               Counting using prints is dicult to control and validate.




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Objectives
        Determine if it is possible
        to reliably detect Adélie
        breeding penguins in
        images

        Generate software to
        (semi-)automate the
        census process.

        Test, using an expert,
        and optimise interactivity.




                                                                       Pygoscelis adeliae)
                                                  Adult Adélie penguin (




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Adélie penguins
        The most abundant and widespread Antarctic penguin

        10 million Adélie make up 80% of the Southern Ocean bird
        biomass

        38% of all Adélie penguins are found in the Ross Sea




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Image capture
        Images captured using a hand-held camera through the open
        doors of a helicopter and/or C-130 Hercules

        Hasselblad H1D with a Phase One digital camera back
               Image size 5440      × 4080,       3-bands natural colour, TIFF
               EXIF data provides date/time and aperture information
               Typical ground resolution better than 0.5 m

        Ten representative images were selected for analysis




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Full-scene example
 5440   × 4080    full-scene




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Sub-scene example
 870   × 510   sub-scene




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Analysis
        Human detection of breeding Adélie not straightforward
        There are many similar-looking objects in the images
        Proposed revised approach:
               Detect the distinctive area of the colony
               Only count penguins within colony area
               Provide software features to easily add/delete penguins




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Colony/background discrimination




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Colony  penguin detection
        Background is largely monochromatic

        Colony area covered in guano and has a red excess over
        green or blue, with higher saturation

        Use linear discriminant analysis to separate colony from
        background, based on:
               Natural colour counts (RGB) converted to hue, saturation,
               lightness (HSL) space values,
               Two-way interactions of HSL space values,
               Aperture setting.

        Classication followed by morphological opening and closing
        dene the colony area

        Penguins detected as dark local minima within colony area

        Penguin objects pruned to upper threshold of circularity
        P 2 / (4πA) to remove long thin objects
        Adopt the centroid of the surviving objects as penguins


IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Original image (350 × 250)




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Detected colony




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Cleaned colony




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Candidate penguin locations




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Overlaid penguins




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Editing facilties
        Detection procedure does not count all real penguins

        False penguins counted
               Non-breeding penguins within colony
               Penguin shadows or spurious dark objects

        True penguins missed
               Breeding penguins outside colony
               Penguins indistinct compared to surroundings

        Editing facilities required:
               Overlap between photographs requires group deletions
               Add or delete individual penguins
               Check that penguins are not double-counted
               Record of editing steps maintained
               Number of editing steps requires single-click operation




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Implementation
        Software written in Matlab 2010b, deployed with Matlab
        compiler

        Census results stored for each captured image in a small le

        Deployed for testing phase to a penguin ecologist

        Second development phase to x faults and improve
        interactive response:
               Reduce memory overhead for each counted penguin
               Reduce keystroke eort for additions/deletions
               Add ability to count penguins within non-guano stained area

        No problems reported after second phase deployment




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Editing software




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Bootstrap colony classication rates




IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Colony classication rates
        Accurate colony delineation is very important

        Requirement is for high true positive, low false negative rates

        About 5% of images give poor results:
               Due to very poor colony/background distinction
               No clear reason for this poor result




       CF001669                                   CF001720



IGARSS-2011, 25-29 July 2011, Vancouver, Canada
Conclusions
        Semi-automated penguin counting is a pragmatic approach

        Laborious counting automated; ne editing left for an expert

        Software allows editing, maintains counts, stores results

        Emphasis is interactive productivity




                                    Acknowledgements
                  Ministry for Science and Innovation (funding).
                 Antarctica New Zealand (funding and logistics).
                        Helicopters New Zealand (ying).
               Squadron 40, Royal New Zealand Air Force (ying).


IGARSS-2011, 25-29 July 2011, Vancouver, Canada

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mcneills_igarss2011_penguins.pdf

  • 1. Semi-automated penguin counting from digital aerial photographs S.J McNeill K Barton P Lyver D Pairman Landcare Research New Zealand
  • 2. Motivation Understanding changes in penguin population is important, as these can be used as indicators of anthropogenic and foodweb eects Aerial photography is used in the Ross Sea (Antarctica) to capture a reliable count of Adélie nesting penguins From 1981, the Ross Sea area (158 175 o o E) has been surveyed annually There are many diculties in achieving this census count: Timing is critical, Ground counting is dicult or impossible, Counting using prints is dicult to control and validate. IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 3. Objectives Determine if it is possible to reliably detect Adélie breeding penguins in images Generate software to (semi-)automate the census process. Test, using an expert, and optimise interactivity. Pygoscelis adeliae) Adult Adélie penguin ( IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 4. Adélie penguins The most abundant and widespread Antarctic penguin 10 million Adélie make up 80% of the Southern Ocean bird biomass 38% of all Adélie penguins are found in the Ross Sea IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 5. Image capture Images captured using a hand-held camera through the open doors of a helicopter and/or C-130 Hercules Hasselblad H1D with a Phase One digital camera back Image size 5440 × 4080, 3-bands natural colour, TIFF EXIF data provides date/time and aperture information Typical ground resolution better than 0.5 m Ten representative images were selected for analysis IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 6. Full-scene example 5440 × 4080 full-scene IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 7. Sub-scene example 870 × 510 sub-scene IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 8. Analysis Human detection of breeding Adélie not straightforward There are many similar-looking objects in the images Proposed revised approach: Detect the distinctive area of the colony Only count penguins within colony area Provide software features to easily add/delete penguins IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 10. Colony penguin detection Background is largely monochromatic Colony area covered in guano and has a red excess over green or blue, with higher saturation Use linear discriminant analysis to separate colony from background, based on: Natural colour counts (RGB) converted to hue, saturation, lightness (HSL) space values, Two-way interactions of HSL space values, Aperture setting. Classication followed by morphological opening and closing dene the colony area Penguins detected as dark local minima within colony area Penguin objects pruned to upper threshold of circularity P 2 / (4πA) to remove long thin objects Adopt the centroid of the surviving objects as penguins IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 11. Original image (350 × 250) IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 12. Detected colony IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 13. Cleaned colony IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 14. Candidate penguin locations IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 15. Overlaid penguins IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 16. Editing facilties Detection procedure does not count all real penguins False penguins counted Non-breeding penguins within colony Penguin shadows or spurious dark objects True penguins missed Breeding penguins outside colony Penguins indistinct compared to surroundings Editing facilities required: Overlap between photographs requires group deletions Add or delete individual penguins Check that penguins are not double-counted Record of editing steps maintained Number of editing steps requires single-click operation IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 17. Implementation Software written in Matlab 2010b, deployed with Matlab compiler Census results stored for each captured image in a small le Deployed for testing phase to a penguin ecologist Second development phase to x faults and improve interactive response: Reduce memory overhead for each counted penguin Reduce keystroke eort for additions/deletions Add ability to count penguins within non-guano stained area No problems reported after second phase deployment IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 18. Editing software IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 19. Bootstrap colony classication rates IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 20. Colony classication rates Accurate colony delineation is very important Requirement is for high true positive, low false negative rates About 5% of images give poor results: Due to very poor colony/background distinction No clear reason for this poor result CF001669 CF001720 IGARSS-2011, 25-29 July 2011, Vancouver, Canada
  • 21. Conclusions Semi-automated penguin counting is a pragmatic approach Laborious counting automated; ne editing left for an expert Software allows editing, maintains counts, stores results Emphasis is interactive productivity Acknowledgements Ministry for Science and Innovation (funding). Antarctica New Zealand (funding and logistics). Helicopters New Zealand (ying). Squadron 40, Royal New Zealand Air Force (ying). IGARSS-2011, 25-29 July 2011, Vancouver, Canada