Photos of the Week – November 11, 2022

Back on October 29, I spent a lovely couple hours across town at Lincoln Creek Prairie. I arrived a little before sunrise and had a little time to scout before the light arrived. That meant that when the sun finally popped above the horizon, I had a couple different subjects picked out to put in front of it. After that, I wandered around trying to find insects (there were a few, including some I photographed but didn’t include here). In between insects, I challenged myself to find other interesting compositions.

I had a great time.

Common milkweed (Asclepias syriaca) pod and seed at sunrise. Nikon 18-300mm lens @300mm. ISO 320, f/14, 1/500 sec.
Tall thistle (Cirsium altissimum) at sunrise. Nikon 18-300mm lens @300mm. ISO 320, f/14, 1/500 sec.
Switchgrass (Panicum virgatum) at sunrise. Nikon 18-300mm lens @300mm. ISO 320, f/9, 1/1000 sec.
Stinkbug on Canada goldenrod (Solidago canadensis). Nikon 105mm macro lens. ISO 500, f/10, 1/100 sec.
Fly and morning dew. Nikon 105mm macro lens and Raynox 250 magnifier. ISO 500, f/16, 1/60 sec.

The sunlight quickly became intense enough that it was hard to do much with it. That bright light means extreme contrasts and less color saturation, among other issues. I wasn’t ready to head home, though, so I fell back on an old trick. I worked along the edges of the skinny prairie patch, using nearby trees as a kind of diffuser. The dappled light coming through those branches was softer and more pleasing and the scattered shadows helped provide clean backgrounds for macro photos.

Common milkweed seed and morning dew. Nikon 105mm macro lens. ISO 500, f/13, 1/100 sec.
Canada goldenrod (Solidago canadensis). Nikon 105mm macro lens. ISO 500, f/11, 1/160 sec.
Canada goldenrod (Solidago canadensis). Nikon 105mm macro lens. ISO 500, f/9, 1/800 sec.
Canada goldenrod (Solidago canadensis). Nikon 105mm macro lens. ISO 500, f/9, 1/800 sec.
Wild lettuce (Lactuca sp.) Nikon 105mm macro lens. ISO 500, f/14, 1/160 sec.
Lead plant (Amorpha canescens). Nikon 105mm macro lens. ISO 500, f/10, 1/500 sec.

Insects certainly weren’t abundant, but they weren’t absent either. Flies were the most common, but I saw several stink bugs, a milkweed bug, a little larva I couldn’t identify, and even a little skipper. I was seeing a lot of spider silk caught on plants but I didn’t find an actual spider until I was almost back at the truck and ready to go home. I got to watch it work on the beginnings of a small web. I wonder if it finished the web or caught anything. Given the scarcity of insects around, its chances of catching dinner seemed low.

Common checkered skipper. Nikon 105mm macro lens. ISO 500, f/13, 1/160 sec.
Common checkered skipper. Nikon 105mm macro lens. ISO 500, f/13, 1/125 sec.
Stink bug on pitcher sage (Salvia azurea). Nikon 105mm macro lens. ISO 500, f/11, 1/200 sec.
Tiiny spiderling on pitcher sage (Salvia azurea). Nikon 105mm macro lens. ISO 500, f/14, 1/125 sec.

There are insects and spiders active all winter, but not very many. Every time I go out this fall, I see fewer and fewer. This is a challenging time of year for photography, at least for the kinds of subjects I like best. In addition to a drop in insect numbers, the color of vegetation is fading from gold to a duller brown and there’s no been no snow yet, and precious little frost.

Even with all that, I spent more than two hours exploring a tiny sliver of prairie a couple weeks ago and am looking forward to doing it again soon. It’s supposed to be pretty cold this weekend, with temperatures getting down to about 15 degrees Fahrenheit. It’s not supposed to be windy though… Sounds like great conditions for a prairie hike! Who’s with me?

Evaluating Prairie Restoration/Reconstruction From The Right Perspective

I recently appeared on a podcast (The Prairie Farm Podcast) and had a great discussion about prairies and conservation that spanned a wide range of topics. One of those topics was the way we evaluate sites where we’ve planted prairie vegetation in former crop fields. This is a topic I think about a lot and it has come up in conversations several times just during the last week or so. I’ve written about it before, including some examples from our sites, but it’s worth hitting again.

If you don’t want to read this whole post, here’s my main point: I think it’s important to judge the success of a prairie planting in the context of how it affects the surrounding landscape. Too often, we fret about which plant species did or didn’t show up from the seed mix or how the soil organic matter compares to nearby prairies. Those factors are interesting, and sometimes important, but can often be distractions from the larger value of restored prairie.

As we strive to save/sustain the prairie ecosystem within fragmented landscapes, our long-term success relies on reducing the extent and impacts of habitat fragmentation. We can do that by planting prairie next to and between remnant prairie patches to increase their size and connectivity. The alternative is to keep pumping time and resources into tiny, isolated prairie parcels. That’s almost surely doomed to fail as they become overrun with tree and invasive species and/or suffer gradual and irreversible losses of native species.

Assuming that’s the goal, then, it’s important to evaluate our planted prairies through that lens of landscape restoration. Too many times, we focus on a new planting in isolation. We look at variables such as plant diversity, the relative abundance of particular plants, or – much less commonly – how the site is being used by animals like pollinators or birds. Most frustratingly to me, we also tend to compare the planting to what we think the prairie in that location used to be like prior to European settlement or to ‘reference sites’ nearby.

Diverse plant communities are an important component of prairie plantings because that diversity fosters ecological resilience and provides habitat for a wide variety of animals. However, the plant community doesn’t have to mirror nearby remnants or match up with historical accounts to be effective.

What’s more crucial to focus on is the impact of a planting on the surrounding landscape. Does the new prairie function as connective tissue between other patches of prairie? Does it increase the effective population size of the plants and animals living in that area? Can species travel through it as they attempt to adapt to short-term and long-term changes in habitat conditions? Rather than focusing within the borders of a planting, let’s look up and see how the planting has affected the neighborhood around it.

Here is an aerial photo showing the arrangement of crop field restoration projects (brown polygons) around remnant prairie fragments. We have spent time testing how effective those plots are in ‘de-fragmenting’ the prairie landscape. A simple first step is to see if animals from the remnant are using the new habitat.

I’ve written before about two competing metaphors for prairie restoration. One is the restoration of an historic building, in which the final product is well-defined and success relies upon getting the building back to its original condition. The second, which fits our ecological objectives better, is the restoration of a city after a disaster. In that case, what matters is function. The goal is to re-establish services like communication, transportation, and law-enforcement. People need access to food, water and shelter, and to be able to get back to work. The city doesn’t have to look exactly as it did before for that to happen.

When we are trying to restore function to a fragmented prairie landscape, we should assess that function, rather than focusing solely on structure. Does a new planting add floral resources to the landscape and provide more choices and space for pollinators to forage? Can small mammal or insect populations in formerly-isolated prairies now interact with each other by traveling through the new habitat? Do we have more and better stewardship options because the combined restored/remnant habitat complex is now bigger?

The soils beneath crop-fields-turned-prairies are obviously going to differ from nearby unplowed remnants. That makes those planted prairie plots different, but not necessarily less effective or successful than remnants. What’s more important is the way they complement and add to those remnants.

As a group, and especially scientists, we have spent a lot of time comparing restored habitats to remnants. Doesn’t it feel like we’ve learned most of what we need to from those comparisons? Those discussions seem a little outdated now.

“See here, the soil organic matter in this restored prairie is going to take many decades to match that of remnants, if it ever does. Alas!”

“I say, old chums, did you notice how different the plant community looks in this planting compared to the remnant next to it? Forsooth, several species appear to be missing altogether!”

I don’t mean to dismiss this kind of work altogether. Those kinds of comparisons can be helpful when we make the case to others that plowing up prairies causes irreversible harm. But in terms of evaluating the success of restoration projects, they can sometimes distract us from more crucial efforts to judge our progress. If nothing else, they can be bad for morale. If we’re trying to recreate history or match a nearby reference site, we’re already doomed to fail. If we’re not trying to do that, why are we evaluating success as if we are?

For those of us doing the restoration work, let’s focus on what we’re really trying to achieve. Unless you’re planting prairie habitat purely for aesthetics or educational purposes, the success of your efforts should be based largely on the new habitat’s contributions to the landscape around it, right? Is the prairie ecosystem better off because of your work?

Quantifying the contributions of a planting to the function of an ecosystem can be difficult, of course. It’s a lot easier to count and compare plants between two sites than to assess changes in the genetic fitness of the plant population or the movement patterns of pollinators between those sites. That’s fine – we can still do our best to design and carry out data collection efforts that give us helpful information. We’ll get better at it over time.

This southern plains bumble bee and the tree cricket in the background both found their way into this restored prairie. At our Platte River Prairies, we’ve seen that a very high percentage of bee, grasshopper/tree cricket, ant, bird, and small mammal species from adjacent remnant prairies are found in our newly-planted habitat. That’s an important initial measure of success.

In the meantime, we can also focus on shifting our mindset so our more casual observations are pointed in the right direction. Are we seeing bumble bees and butterflies from adjacent remnant prairies use our new habitat? Has the neighborhood coyote family incorporated the new planting into its daily hunting pattern? Do we see new grassland bird species showing up that might have avoided the area previously because of the limited prairie size?

Prairie restoration is challenging. It’s also awfully important. The biggest reason it’s important, though, is that – at least in fragmented landscapes – it’s really the only hope we have for conserving prairies and the species that rely on them. We don’t have to convert the whole landscape back to prairie, we just have to create habitat patches large and connected enough to be resilient and support viable populations of most species.

As we chip away at the problem, let’s make sure we’re learning as much as we can along the way. We’ve spent a lot of time comparing our planted prairies to remnants. Now let’s concentrate a little more on comparing prairie landscapes before and after we’ve added prairie plantings to them. After all, that’s the information we need to improve and adapt our restoration methods going forward.