Source: ATOLLA TECH LLC submitted to
A NEW METHOD FOR REAL-TIME TRACKING OF POLLINATORS – QUANTIFYING HONEYBEE AND NATIVE BEE ACTIVITY
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
1030505
Grant No.
2023-33530-39688
Cumulative Award Amt.
$175,000.00
Proposal No.
2023-00954
Multistate No.
(N/A)
Project Start Date
Jul 1, 2023
Project End Date
Jun 30, 2024
Grant Year
2023
Program Code
[8.13]- Plant Production and Protection-Engineering
Project Director
Dagan, M. S.
Recipient Organization
ATOLLA TECH LLC
184 MAPLE AVE
ROCKVILLE CENTRE,NY 115704373
Performing Department
(N/A)
Non Technical Summary
At Atolla Tech we are proposing a new method for assessing the pollination efficiency of different bee species in real-time thereby aiding growers in optimizing pollination of their crop whether they rely on wild pollinators or use honey bee services or both. Our technology includes a lidar and machine learning (ML) algorithm that detects, identifies, and tracks pollinator species in real-time. Their flight activity will be viewable on a live map and a Pollination Visitation Index (PVI) level will be provided at the end of the day. The PVI will provide the grower with a summarized activity level that will be represented as a value between 0 and 1, where 0 represents no pollination activity and 1 represents high pollination activity. The PVI model will be developed under the SBIR phase I proposal and then analyzed at the end of the season. Automating the pollination efficiency/success using a remote sensing in real-time approach will allow for optimization in pollination practices. It opens the possibility for quantifying wild bee and honey bee levels in real-time, thereby optimizing the timing, duration, and placement of honey bee hives each season. In this trial, it is our goal to understand how much of a need there is for honey bees in Southeast blueberry. Specifically, whether placing honey bee colonies in blueberry orchards is worth the investment or are native, local pollinators (e.g., southeastern blueberry bee) that are adapted to blueberry sufficient.
Animal Health Component
80%
Research Effort Categories
Basic
0%
Applied
80%
Developmental
20%
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
13630102020100%
Knowledge Area
136 - Conservation of Biological Diversity;

Subject Of Investigation
3010 - Honey bees;

Field Of Science
2020 - Engineering;
Goals / Objectives
Major goalof this project: Determining a working methodology for quantifying a Pollination Visitation Index using Atolla's prototypelidar (described in patent WO2021138586A1) and ML algorithm.Technical ObjectivesTO1: Design an experiment for determining honey bee visitation of blueberry under controlled settings.What is the necessary size for the honey bee colony with respect to the greenhouse so that the pollination data is not a saturated data set (too little planted crop/ too large of a colony size), thereby skewing the upper bound of the index?What are the variables that may affect the measurement of pollination success and how can they be minimized in the experiment design, e.g., weather, pests, pollinators other than honey bees?What modifications are necessary in the greenhouse for optimal control in the experiment?TO2: Define Pollination Visitation Index (PVI) and the methodology for determining it.Assuming a scale of 0 to 1 for the PVI, what do we define as 0 and what do we define as 1? How will the gradient be defined?How will the PVI be comparable to the manual measurement of pollination success using the state-of-the-art method?How much will variables change from year-to-year? How will that be factored in the model when repeating the experiment over the next season?How do we account for and then factor out any variables that may skew the data such as pests and weather. What assumptions will need to be made in the PVI model.
Project Methods
Technical Objective 1: Establish a baseline of honey bee visitation of blueberry under controlled settings.Design experimental setup in greenhouse. To optimize the accuracy of the results, outside variables affecting the calculation of PVI and the manual measurement of pollination success need to be minimized. Variables of concern are those that are difficult to isolate and subtract out and therefore could skew the data due to their inconsistency through the season as well as from season to season. Such variables (e.g., climate, pests, pollinators other than honey bees) could cause changes in yield and fruit size that could be incorrectly attributed to the pollination efficiency. To minimize the effects of these variables, we will:Set up experiments in a closed greenhouse- weather-controlled, if possible. Use potted plants and drip irrigation. Add a net on any vents where honey bees can exit.Experimental setup will be optimizated and recorded for repeatability. A second replicate within the same blueberry season will be added in the greenhouse using Rabbiteye blueberry varieties. These varieties bloom later than SHB, therefore two Rabbiteye varieties will replace SHB plants when bloom is finished.Determine the size of the honey bee colony necessary for the greenhouse used in this project, or the ratio of honey bees to greenhouse area (HGR). Determining the appropriate quantity will avoid a saturated data set. Too large of a colony size would result in an unreliable upper bound of the PVI. The necessary ratio of honey bee colony size to greenhouse size, HGR, will be assessed using results from previous studies in greenhouse environments as well as expert recommendations for blueberry.Approximate the HGR based on previous studies. In the early 2000's, Winston et al. examined the feasibility of using honey bees for greenhouse tomato pollination. They used small colonies (i.e., nucleus of 5 frames). A strong nucleus colony will have about 5000 bees in it. These studies could provide an initial model for determining colony size.In blueberries, it is recommended to place two honey bee hives per acre - where each acre consists of about 3,000 plants. If we know the plant age, then we can estimate the number of flowers that will bloom. We can then scale this recommendation to fit our greenhouse. We will assume that two colonies is about 50,000 honey bees. Each acre contains roughly 3000 plants each with 1000 flowers or 3M flowers/acre. Not all 50,000 bees are foragers (about 1/3 are) and not all foragers will visit the blueberry crop. However, with these assumptions, we can get a rough estimate.Using the estimated HGR, we will setup a colony of bees accordingly. Once the results of the season are analyzed, then we can choose to adjust the HGR slightly when repeating the experiment, all while recording/noting each change in detail.Technical Objective 2: Develop a technique for estimating the efficiency of pollinators in real-time using Atolla's lidar and ML algorithm.Implement a peer-reviewed method for measuring pollination efficiency such as that described in Standard methods for pollination research with Apis mellifera (Delaplane et al. 2013).Pollination success is typically measured as the ratio of ripe fruit or seeds relative to the initial number of available flowers or ovules. We will be using blueberries which relies on cross-pollination, the transfer of pollen to the stigma occurs between genetically different plants. [10]Implement the methodology described in section 2.2.2 of Delaplane's paper as a baseline for our manual measurement pollination success. Like in the paper, flowers will be bagged with netting before and after honey bee visitation to control pollination occurrences. However, unlike the paper suggests, data will also be collected during overcast/inclement weather for more information on pollinator behavior. Record/note the plan in detail.Compare data collected by the technician to recorded lidar data.Determine the assumptions that will need to be made to account for and then factor out any variables that may skew the data (i.e., pests and weather). Experiment will be in a greenhouse to limit pest and weather effects.Record observed weather and any identified pests to correlate to the pollination results. Ideal conditions for honey bee forage include air temperatures >55F and clear skies. Based on this information, we will adjust the number of forage days. We can also predict whether a freeze event damages blueberry flowers, making them less attractive to pollinators.Continuously scout, identify, and take note of any pests affecting the crop. Correlate to the pollination results. Pests are likely not as much of a problem leading up to and during bloom, but rather after. We can control for pests after bloom using conventional IPM.Measure the pollination success using the method described by Delaplane et al.. Identify any gaps and needs as they arise.Model the pollination visitation index (PVI) using the lidar data. Identify gaps/needs as they arise.Establish a pollination visitation index on a scale from 0 to 1 where PVI =0 will be defined as no pollination activity. This index score will be derived from the minimal number of flower visitations. When the PVI reaches a level of near or at 0 for a certain time period (needs to be determined), then it can be recommended to the grower that the honey bee hives are no longer necessary. To identify PVI=0, flight activity levels of the honey bees will be measured while there is no bloom. How that is represented in the data for honey bees and how that should be quantified will need to be explored.Use maximum flight activity to establish PVI=1 or the highest level of visitation observed by Atolla's system and confirmed by fruit set. After a full season of data, identify what 1 means. Maximum flight events will be used to determine 1. This upper bound may be adjusted after repeating experiment for multiple seasons.Assuming a scale of 0 to 1 for the PVI, determine the gradient for flight activity levels. Results of PVI over the course of a bloom period should resemble a bell curve-type gradient. Low on both ends (start and end of bloom) and then a peak in the height of the bloom where pollination activity approaches a maximum of 1.Replace SHB plants when bloom is finished with two Rabbiteye varieties. Repeat 2.1 - 2.4.Identify gaps/needs as they arise.Compare the season long PVI data to the pollination success calculation determined by the method described in Delaplane et al. Work with USDA experts in determining the appropriate recommendations and conclusions that will be derived from the data.Plan for repeating experiment in the following season and develop phase II plan. Determine which variables are expected to change when repeating. Account for those expected changes.

Progress 07/01/23 to 06/30/24

Outputs
Target Audience:Our phase I project, focusing on tracking and quantifying the pollination behavior of honey bees, targeted farmers that grow crops which require managed bee pollination. To develop our deep-tech solution, we partnered with the USDA under a CRADA. This work is particularly relevant to the USDA Agricultural Research Service (ARS) given its mission to ensure agricultural productivity and sustainability. By examining the specific interactions between honey bees and these crops, the study provides crucial insights into optimizing pollination strategies to enhance crop yields. Understanding bee visitation patterns can lead to improved cultivation practices that maximize pollination efficiency. In blueberries, for example, pollination is critical for fruit set and quality. Our findings can inform ARS initiatives aimed at supporting and enhancing bee populations and health, thereby ensuring robust pollination services. This research aligns with the USDA ARS's goals of advancing agricultural science and promoting the health of pollinators, which are vital for the success of diverse agricultural systems. This work will then be commercialized for small and medium sized farms that are looking to reduce the use of managed honeybees and increase the reliance on native bee populations. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?We hired a technician under this phase I that is being trained to use our lidars and service them. USDA ARS has trained an intern to work on this project and collect our scouting data. How have the results been disseminated to communities of interest?We have not yet published, however, we are starting to see results which will be used for future papers by the USDA ARS group. We have started sharing our results with potential commercial partners/customers and are moving towards a commercial trial. We have also gained interest from honey makers and apiaries as a result of the phase I outcomes. What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? TO 1 We started our field trials with blueberry potted plants, which were placed in a greenhouse with three tables. Each table fit 50 4-gallon potted plants per table and was kept under drip irrigation. Although we planned on blueberry being our main crop for the trials, we encountered challenges due to limited flowering from these young blueberry plants, resulting in low bee activity. Consequently, we adjusted our approach for the Phase I experiment, opting to use African basil plant, as suggested by the USDA. This decision was made to ensure adequate floral resources for bee attraction and activity. To ensure a controlled trial, we took several measures to reduce the number of variables that may affect our results. To prevent any pollinators other than the European honeybee from affecting the trial, we set up our experiment in a temperature-controlled greenhouse at the USDA site. We used a fully enclosed greenhouse to ensure that the honeybees we placed there were the only ones pollinating and sealed off any openings to prevent any from leaving. The greenhouse uses drip irrigation and has temperature controls that we could monitor. We also implemented our own sensors to monitor environmental variables such as temperature, relative humidity and dew point. While the temperature in the greenhouse was set to maintain itself at a constant 80°F, we instead found it fluctuating quite a lot. Data from December 8th, 2023 showed the temperature in the greenhouse fluctuating by almost 20°, and as expected, our lidar's bee activity data correlates with those fluctuations. This was seen throughout our dataset, with the highest activity usually taking place in the afternoon. We believe that the ramp up of activity in the afternoon also has to do with the location of the greenhouse. The greenhouse only has two transparent walls, thereby its orientation causes a significant increase in sunlight entering into the space in the afternoons. The size of the honey bee colony necessary (the colony size to greenhouse size ratio - HGR) was estimated for the 50 by 25 ft greenhouse that we used. The initial colony size was projected based on previous studies as well as expert recommendations. Since we did not find any studies that used honey bees in a greenhouse (greenhouses typically use bumble bees), we based our initial estimate on what is typically used in outdoor blueberry crops, downsized slightly based on the recommendation of the USDA entomologist. That initial estimate turned out to still be too large and eventually we brought it down to only 2 frames. TO 2 To implement a method for PVI, our team optimized our feature engineering algorithms and made necessary adjustments to our ML code to facilitate automated bee detection within a greenhouse environment. A comprehensive data collection protocol for LiDAR-based bee detections was established, configuring our optics and data acquisition systems to capture relevant information. Field trials were then conducted to validate the accuracy and reliability of these automated detection algorithms. This validation process involved comparing automated detections with manual observations. During the experiments, USDA personnel would record their scouter data multiple times each day. Their method for scouting pollination activity included walking a certain predetermined path through the greenhouse rows and manually recording sightings of bees near flowers. They would mark down the number of bees seen and the position where they were spotted. The collected USDA data was filed in a logbook and then shared with our team. We uploaded the data into our database and then normalized it to values between 0 and 1, which was then compared to our pollination visitation index (PVI). For our PVI calculations, we consider other variables that help us exclude false positives while keeping our thresholds sensitive enough to capture a high number of true events. Those include the time of day, temperature, and intensity of light. For example, a positive bee event seen at 3pm will be weighted differently than a hit at 1am. We know from empirical data that bee activity in the middle of the night is not common, albeit not impossible, and so we established a methodology for assigning weights to the different variables at play. As a result, the PVI is a quantitative measure designed to assess bee pollination activity within a certain environment. We use a normalized value between 0-1 so that we accurately compare the pollination activity across the different scenarios, and as a result the PVI offers a comprehensive perspective on pollination dynamics. A higher PVI value indicates a greater frequency of bee visits, reflecting heightened pollination activity. We define the normalized PVI as: PVInorm=(Xi-min(X1:Xn))/(max(X1:Xn)-min(X1:Xn)) Where i refers to the index of an observation interval out of n intervals, beginning at i=0, and Xi is defined as the weighted number of detected bee events during interval i: Xi= NB(Ot)× wT(T)× wh(h),×wt(t)) And where NB is the number of bee detections, Ot is the duration of an observation interval, wT is the weight assigned to temperature, T is the temperature, wh is the weight assigned to humidity, h is the humidity, wt is the weight assigned to time of day, and t is the time of day. Defining PVI=0 involves comprehensive monitoring and data collection during no bloom periods to establish a baseline of non-pollination activity. This process includes systematically observing and recording honeybee behaviors, utilizing automated detection systems to continuously monitor flight activity and flower visitations, and conducting thorough observations when no flowers are in bloom. During a 20-minute scan of our system, if zero bees are detected/sighted we would define this as PVI = 0 (i.e there was no pollination activity, even though there are still bees onsite). We define PVI=1 as the maximum number of honeybee detections recorded by both the USDA partner and our system during a full season of data collection. This threshold may be refined after collecting and analyzing more data across multiple seasons, ensuring a robust and accurate representation of PVI=1. The maximum value will vary between different environments, crops, and seasons. Therefore, as we increase the number of data trials, our max ('1') will become more accurate and we will likely have different max values set for different crops or terrains. By analyzing peak detection data and establishing this upper limit, growers can quantify the maximum pollination potential. When we execute the correlation function in Excel to get the correlation value between our data and the USDA, we found that we had a correlation value of 0.70 (1 being perfect correlation, and 0 being absolutely no correlation). We also checked whether there was a correlation between PVI and temperature. The results from achieving our Phase 1 technical objectives demonstrate the technology's capability for measuring pollination efficiency in real-time. Under this phase I project, we successfully established a robust data collection protocol and developed accurate algorithms for automated bee detection. Moreover, our analysis revealed correlations between bee activity and environmental factors, providing insights into bee movement patterns and foraging behavior within the greenhouse. In conclusion, the Phase I project has demonstrated the technical feasibility of using LiDAR technology to quantify bee pollination activity in a greenhouse environment. Moving forward, we will refine our methodology and extend our research to larger-scale field settings. We anticipate that our approach will yield valuable insights into pollination dynamics and contribute to the broader understanding of ecosystem health and biodiversity conservation. ** Figures that were referenced in this text can be provided.

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