Documents / Official release
This is a 2023 draft research paper by Richard M. Medina and Simon Brewer of the University of Utah and Sean M. Kirkpatrick of the Department of Defense, prepared for journal submission and released in full by AARO in 2025. It analyzes 98,724 NUFORC public sighting reports from 2001 to 2020 by county with a Bayesian model. It finds that more light pollution and tree canopy mean fewer sightings, while more air traffic and military area mean more. Cloud cover showed no relationship.
025 Military installations – Military installation data are sourced to U.S. Census TIGER/Line shapefiles and downloaded from data.gov (data.gov, 2022). The U.S. Census created this dataset in collaboration with the U.S. Department of Defense and the U.S. Department of Homeland Security. The data represent the boundaries of military installations. For this research, those boundaries were overlaid onto U.S. counties, where the area of each county that is military installation is calculated. Models The NUFORC dataset is first explored alone to identify general spatial patterns of reported sightings using hotspot analysis. This exploratory analysis is based on the Getis-Ord (Gi*) index. This index identifies significant clusters of low values (cold spots) and high values (hot spots), by comparing the aggregate number of population standardized sightings in a set of neighboring counties to the full distribution of counts (Getis and Ord, 1992; Ord and Getis, 1995). Different from a heat map, the resulting map shows statistically significant regions of high and low occurrences. To model potential for seeing UAPs we use Bayesian small area estimation, based on the relative rate of sightings in the population of an area. Small area models are commonly used in epidemiology to study the spatial pattern of diseases. These incorporate a spatial autoregressive term to limit the influence of extreme values, which are often linked to small population sizes. For this model, the count of reported sightings for county i is assumed to follow a Poisson distribution as follows: 𝑦𝑖 ∼ 𝑃𝑜𝑖𝑠(𝜃𝑖𝐸𝑖 ) Where 𝐸𝑖is the expected number of sightings for county i and 𝜃𝑖 is the relative rate. To get the expected value, first we estimate the per capita rate of sightings for the entire study region as the total number of sightings divided by the total population. The expected value for any county is obtained by multiplying this value by the population of that county. Where 𝜃𝑖 > 1, the number of sightings is greater than would be expected based on population alone. Finally, the set of relative rates are modeled as follows: log(𝜃𝑖) = 𝛽𝑋𝑖 + 𝜖 Where 𝛽𝑋𝑖 is the set of z-score transformed covariates representing visibility and air traffic described above with associated coefficients. Finally, the model error (𝜖) is decomposed into a spatial autoregressive effect and non-spatial random noise. Model parameters and coefficients are estimated using Integrated Nested Laplacian Approximation (Rue et al., 2017). Model results are reported as the mean of the posterior probability distribution for each coefficient (Table 1) and spatially as the probability of a counties relative rate being over twice the national average (Figure 4). Variance Inflation Factors (VIFs), which signal potential multicollinearity within aPage determined to be Unclassified Reviewed by Chief of Staff, AARO IAW FY24 NDAA, Section 1841 (a)(1)(C) Date: 02/06/2025
Official release, from the nara collection. The PDF is mirrored here; the original link is above. 16 pages are in the text index: search them above, or from the library's search.