Astute contributors to Snapshot Wisconsin may have noted that one of the primary partners on the project is NASA. Yes, that NASA, known for space-flights and Neil Armstrong. For many people, the involvement of an air and space agency with a wildlife monitoring project may not be intuitive. Here’s how NASA and Snapshot Wisconsin work together:
NASA doesn’t just focus on our sun, solar system, and broader universe. It also has a dedicated Earth Science branch that houses research related to our atmosphere, weather, energy cycling, and ecosystems. This branch aims to predict change over time in, for example, energy cycling or biodiversity resources.
Some things, like animal population processes, are incredibly difficult to track across large spatial areas. Even with all the Snapshot Wisconsin cameras out on the ground, the total physical area in which we are observing animals is fairly limited – a point where each camera is, with a lot of space in between points. What we need to do is fill in the data gaps between camera locations. In other words, we need to be able to make predictions about areas where we don’t have observations. And this is where NASA comes into play.
NASA maintains a number of satellites that orbit Earth. These satellites carry on-board sensors that record light reflectance off of the Earth’s surface at different wavelengths. The images these satellites take of the Earth’s surface can be used to determine, for example, the locations of different landcover types (forest, wetland, prairie, etc.), or where leaves are growing or senescent, or where and when there is snow-cover. What’s great about these sensors is that they take photos regularly, and over large continuous spaces, so we can collect these data from our trail camera locations AND the spaces in between them.
Two of the more important sensors for our research are the Landsat and MODIS sensors. Landsat images have a spatial resolution of 30 meters (think of this as a pixel size – each pixel is 30 m by 30 m) and a temporal resolution (i.e., gap between flyovers) of 16 days. MODIS images have a spatial resolution of 250 – 500 m, and a temporal resolution of 1-2 days. These sensors are complementary—MODIS’s greater temporal resolution makes it more useful for detecting temporal environmental changes like plant green-up, while Landsat’s greater spatial resolution makes it more useful for detailed mapping of relatively static environmental attributes, like the location of forests, wetlands, and prairies.
How do we use satellite data and trail camera data together? We determine the association between the number of animals we count in trail camera photos and a series of environmental variables taken from satellite data. Understanding these associations gives us an idea of why animals might be more or less abundant in some places than in others, and allows us to suggest actions managers might take. For example, we might find that prairie chickens are highly associated with prairies but not with forests, and so we might suggest removing trees that are encroaching upon prairie land in order to increase prairie chicken numbers.
Without images collected from space, it would be incredibly difficult to reliably predict and map the distribution and abundance of species.
One of the most common (but generally unfounded!) critiques of citizen science is that data collected by citizens may not be as reliable as data collected by professional scientists. We are currently wrapping up an analysis of image classification accuracy, and the evidence suggests that the crowd-based species consensus is generally very accurate. Keep up the great work! Read More…
How seasonality influences where animals are located is a major scientific focus of Snapshot Wisconsin. Animals move around, so their distribution in space changes through time. Animals also tend to have different phenophases – characteristics associated with specific seasonal or annual environmental phenomena (think spring or fall migration) that can influence how often they are detected by cameras.
A classic phenophase found in mammal species is torpor or hibernation, and bears provide an excellent local Wisconsin example. Whether bears are ‘true hibernators’ or not is often debated. Compared to many smaller mammals that drop their body temperature to near freezing, bears scarcely depress their body temperature at all. Furthermore, small mammals tend to sporadically emerge from hibernation throughout the winter to pass metabolic waste and eat a little…bears do not. Most amazingly, bears can go all winter without eating or moving without substantial muscle atrophy: unlike humans or most other mammals, bears can synthesize new proteins out of the nitrogen contained in their urea. While other animals wake up to pass waste, bears turn this waste into new muscle tissue.
One way in which Snapshot Wisconsin can contribute to our understanding of bear ecology beyond measures of bear distribution or cub production is by providing information regarding the timing of when bears seem to be active. Bears are clearly more regularly photographed during summer and early autumn than during winter:
The pictures provide an indirect cue as to how bears are behaving and the timing of their hibernation. This information can be used to evaluate hypotheses regarding variation in bear hibernation behavior–for example, there is some evidence that bears living in close proximity to humans and human food sources enter hibernation later than bears primarily consuming wild foods.
Seasonal patterns in wildlife images can also provide useful population-level information. Let’s visualize the photographic rates of a species that does not practice hibernation, deer:
There is a less pronounced seasonal pattern (a large drop in June reflects a slightly unbalanced effort across the year–many cameras were being set up at this time in 2015). Still, there is a drop in late winter and early spring that is consistent with what we know about the annual population dynamics of deer in the state–most adult deer die during late winter, and late-winter abundance should always be lower than pre-winter abundance (for comparison, one can find estimates of deer abundance based upon harvest metrics here and here). The number of pictures taken during any one time period is subject to a lot of variation beyond changes in population size, and we do not imply that a 50% increase or decrease in the number of pictures corresponds to a 50% increase or decrease in the number of animals. However, the count and timing of pictures is an input for statistical models that can correct for other sources of variation and be used to formally estimate things like changes in population size.
Two seasons of Snapshot Wisconsin are now in the books! As you may recall, the first two seasons focused primarily on images from concentrated camera grids located around two focal areas where elk exist.
Both areas are predominantly forested, but differ slightly in terms of climate and vegetation species. Animal-wise, we would also expect some minor differences in community:
…and we find a few things. One surprise is some indication that Cottontail rabbits were photographed more frequently further north. This may be a case of confusing rabbits and hares in their summer coats, but results above have not yet been filtered by any agreement metric. Less surprising: there were more elk pictures at the northern Wisconsin site (elk herds are just getting going in central Wisconsin), and also more bear and snowshoe hare pictures up north as well. (Of course, deer are predominant). Generally speaking, these two areas are fairly similar, and one exciting development (forthcoming next season) is project expansion across a broader extent of the state.