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  Archived Posts From: 2022

beneficial-use

Wildlife Cameras as a Wetland Monitoring Tool: Birds in the Marsh

Written on: May 25th, 2022 in Beneficial UseWetland Restorations

By Kayla Clauson, DNREC’s Watershed Assessment and Management Section

Wildlife cameras are a tool scientists can use to collect wildlife field data. Often, scientists go out in the field and conduct monitoring that gather similar data but are restricted because they only get a small snapshot of their target observations. For example, a field crew will observe all birds using a salt marsh during marsh bird surveys, which are conducted early morning at sunrise when there is low tide. This typically gets done three times a year, when birds are likely to be most active. Using wildlife cameras allows scientists to capture birds that are using the project area during the entire year, all hours of the day and night. Although wildlife cameras are not a perfect tool, they allow scientists to actively capture data with minimal disturbance to the animals as well as gather data over a longer period.

The target of this monitoring is to better understand wildlife habitat utilization at both our reference (salt marsh) and project (mudflat) sites. The goal is to see how animal usage may compare long-term between the two sites before marsh recreation occurs (current), during the reconstruction and afterwards. To get a better understanding of the entire project and other current monitoring, check out this previous blog post.

Images from the wildlife cameras at both the reference and project site.

Our wildlife cameras have captured a variety of both mammals and birds. Let’s take a look at the birds we’ve captured for now.

Duck, Duck, Goose…

Family: Anatidae – Ducks, Geese, Swans.

Although waterfowl aren’t the primary targets of this study, we capture a lot of interactions of birds in the Anatidae family. Some of the common Anatidae family we’ve captured are Canada Geese (Branta canadensis), Mallard (Anas platyrhynchos), Green-Winged Teal (Anas crecca), and Hooded Merganser (Lophodytes cucullatus). These birds can be seen mostly around high tide, while swimming or eating.

Figure 2. Honk (goose) and Tonk (gander) are nesting in front of this camera. Notice how Honk is the assumed primary aggressor/protector during mating season.
Figure 1. Green-winged Teal (top left), Mallard (top right), Canada Geese (bottom left), and Hooded Merganser (bottom right).

Anatidae Highlight

There has been a Canada goose pair nesting at our reference site. They have been named Honk and Tonk. Honk is the male goose (gander) and can be distinguished in most of the photos as he is a fierce protector of his female partner, Tonk. While she is incubating, she won’t be leaving her nest often until her eggs hatch. Since they are nesting in front of the camera, many of the captures at this site will be of them and can skew our data. However, scientists can use their best judgement on data recording of these two individuals.

What’re you laughing at?

Family: Laridae – Gulls, Terns, Skimmers.

The second most common birds we see a lot of are gulls and terns. Gulls can be seen in the project area mostly at low tide foraging on the mudflat. Gulls can be challenging to identify due to similar morphology, coloration, and juvenile plumage. For data collection gulls were identified down to their family name (Laridae), except for Laughing Gulls (Leucophaeus atricilla). Named for their laugh-like call, Laughing Gulls are easily distinguished from other gulls because of their black head. In addition to Laughing Gulls, some common gulls and terns include Herring Gulls (Larus argentatus), Ring-billed Gulls (Larus delawarensis), Forster’s Tern (Sterna forsteri), and Common Terns (Sterna hirundo).

Laridae Highlight

Terns are known for their aerial dives when foraging for fish below the waters surface. Although terns are not typically found walking around the mudflat like gulls, we’ve been fortunate enough to capture some of their aerial dives on camera with a big splash!

Heron Paparazzi

Family: Ardeidae – Herons, Egrets, Bitterns

The third most common family we observe are herons and egrets in the Ardeidae family. One of our most seen birds during our monitoring are Great Blue Herons (Ardea herodias). We’ve also captured Great Egrets and Snowy Egrets- but with a lot less captures. We hope as the cameras remain out, we will capture more secretive marsh birds, such as the Least Bittern or American Bittern.

Figure 5. From left to right we see Great Blue Heron, Snowy Egret, and Great Egret at both sites.
Figure 6. Great Blue Heron observing the camera and seemingly showing off.

Ardeidae Highlight

Standing about four-feet tall with a six-foot wingspan, Great Blue Herons are quite the impressive bird. Known for their huge size and stalking behavior alongside coastlines and waterways, they also turn out to be quite photogenic. Many photos captured include Great Blue Herons observing the cameras closely, seemingly posing, or showing off the large fish they can catch.

Talon-ted birds

Family: Accipitridae- Hawks, Eagles, Kites

The last birds to discuss that are often captured in our project are hawks and eagles. We are fortunate enough to have captured Northern Harriers (Circus hudsonius) and Bald Eagles (Haliaeetus leucocephalus). We see Northern Harriers flying low along the marsh looking for prey, such as small mammals, in the grasses. Bald Eagles can be spotted soaring with fish or showing off their talons.

Figure 7. Bald Eagle with fish (top) and Northern Harrier soaring with distinguishable white patch on back (bottom).
Figure 8. Bald Eagle Adults (top left and right) and juvenile (bottom left and right). Notice the wing and head feather differences between adults and juveniles.

Accipitridae Highlight

Best known for their patriotic symbolism for the United States of America, Bald Eagles are a frequent capture at our reference and project sites. We can distinguish both adult and juvenile Bald Eagles from each other based on the coloration of the feathers. Adult bald eagles are dark brown with a white head and tail, whereas juveniles are fully brown in coloration and do not have a fully white head until about 5 years of age.

Birds of a Feather

Some other birds we capture are Yellow Legs (Tringa melanoleuca), Clapper Rails (Rallus crepitans), Turkey Vultures (Cathartes aura), and Cormorants (Nannopterum auritum). Yellow legs belong to the family Scolopacidae, while Clapper Rails belong to Rallidae. These are both birds that directly utilize the marsh for hiding and foraging. Cormorants in the family Phalacrocoracidae are seen swimming at high tide and Turkey Vultures in the family Cathartidae are seen scavenging for food.

Figure 9. Turkey Vulture (top left), Cormorant (top right), Yellow Legs (bottom left) and a pair of Clapper Rails (bottom right).

Stay tuned to learn more about what we capture on our wildlife cameras next time when we explore mammals on the marsh!


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wetland-assessments

Planning a Brighter Future for the Wetlands of Delaware’s Inland Bays

Written on: May 25th, 2022 in Wetland AssessmentsWetland Restorations

By Erin Dorset, Delaware Division of Fish and Wildlife

An expansive tidal wetland in the Inland Bays.

The Inland Bays are a beautiful and beloved part of Delaware, containing about 20% of the state’s wetlands. Those wetlands are important economically, culturally, and ecologically, as they improve water quality, support commercial and recreational fisheries, support tourism, absorb flood waters, and provide crucial feeding and nursery habitat for wildlife. However, the Inland Bays are also home to agriculture and booming development, and sea-level is projected to keep rising in the region, all potentially having negative effects on wetland acreage and health.

In light of all this, DNREC’s Wetland Monitoring and Assessment Program (WMAP) recently investigated the major problems that wetlands in the Inland Bays face and the best paths forward to ensure that wetlands in the bays are around for generations to come, creating an Inland Bays Wetland Restoration Strategy. To do so, WMAP gathered relevant existing data and reports, including their own tidal and non-tidal Inland Bays wetland condition reports, used expert input to list out the major issues and potential solutions, and used GIS mapping software to identify prime spots where wetland restoration could make improvements.

The Issues

Within the Inland Bays Wetland Restoration Strategy, WMAP identified the major issues that tidal and non-tidal wetlands face in the Inland Bays. They include:

  1. Sea-level rise and land subsidence: The Mid-Atlantic region, including Delaware, is known as a hotspot for sea-level rise, meaning that waters are rising faster here compared with many coastal areas in the U.S. On top of that, land on the Delmarva peninsula is sinking, or subsiding, making the effects of sea-level rise even more pronounced. Sea-level rise and land subsidence can lead to tidal marsh edge erosion and drowning.
  2. Marsh migration barriers: Tidal wetlands can shift inland naturally, or migrate, in many places as sea level rises, provided there are undeveloped lands with gentle slopes. With development increasing throughout the Inland Bays, opportunities for wetlands to migrate inland and save themselves from eroding and drowning are shrinking.
  3. Invasive species: Both tidal and non-tidal wetlands suffer from the presence of invasive plant species, such as the European reed (Phragmites australis), Japanese honeysuckle (Lonicera japonica), and multiflora rose (Rosa multiflora). Invasive plants displace native ones, degrading wetland health and habitat quality.
  4. Hydrology alterations: Ditching has heavily affected tidal and non-tidal wetlands in the Inland Bays. Ditches alter the natural movement of water through wetlands, which can reduce wetland health and negatively affect many plant and wildlife species that depend on natural conditions. Stream straightening or deepening (channelization) is also a problem in many non-tidal riverine wetlands, a practice which can increase stream bank erosion and disconnect floodplains from streams.
  5. Habitat loss and fragmentation: It is estimated that about 60% of the wetlands that once existed in the Inland Bays have been converted and lost, and losses have been especially pronounced for non-tidal wetlands. Most losses are attributed to development, land clearing, and agriculture. Once wetlands are destroyed, so too are their beneficial functions, such as floodwater storage and water quality improvement. Wetlands that remain are becoming more isolated as losses continue, fragmenting important habitat and making it more difficult for wetland-dependent wildlife to survive.
An aerial view of extensive grid ditching in tidal wetlands in the Inland Bays.

A Path Forward

After reviewing the worst issues that wetlands are dealing with in the Inland Bays, WMAP outlined tactics in the restoration strategy that are likely to be the most effective at tackling those problems:

  1. Promote nature-based solutions: Wetland restoration projects that aim to resemble natural conditions tend to be the most effective at restoring wetland health and function, and such projects would help combat wetland losses due to sea-level rise and erosion. For example, living shorelines can increase wetland resiliency against erosion and sea-level rise while absorbing wave energy and creating wildlife habitat. Another option is the beneficial use of dredge material, which can return sediment to drowning tidal marshes, giving them an elevation boost to help wetland plants, wildlife, and functions persist as sea-level rises.
  2. Restore natural hydrology: Many potential actions could help address the widespread hydrology alterations in wetlands throughout the Inland Bays. Ditches in tidal and non-tidal wetlands could be filled in and stream channelization could be reversed, allowing for more natural water flow. Tax ditches could be improved ecologically by adding curves to channels, planting more trees along the sides, and minimizing mowing alongside them.
  3. Improve land use planning: By thinking ahead, many wetland losses and impacts can be avoided. For example, by incorporating marsh migration and sea-level rise into future development and infrastructure planning, building can be prevented in key wetland migration pathways to ensure that wetlands persist, and property and infrastructure flooding challenges can be avoided. Natural buffers should be maintained adjacent to tidal and non-tidal wetlands when considering future development to maintain important wildlife corridors and reduce flooding risks near developments and infrastructure.
  4. Preserve wetlands with easements or land acquisition: Land purchases and conservation easements are tactics that can preserve tidal and non-tidal wetlands for decades and help protect them from certain stressors. Lands that are highly suitable for marsh migration inland (e.g., undeveloped lands with gentle slopes) should be prioritized, as should natural areas that can connect fragmented forested wetland habitat patches. Funding should be secured to support such purchases, and landowners should be educated about their conservation options, such as the Conservation Reserve Enhancement Program (CREP), Working Lands for Wildlife Program, or Forestland Preservation Program.
  5. Control invasive species: Controlling invasive species would improve wetland health and create space for more beneficial native species. The European reed (P. australis) should be treated in tidal wetlands as well as in marsh migration corridors. Landowners should be educated about DNREC’s Phragmites Control Cost-Share Program as well as how to identify other invasive plants and replace them with native species.
  6. Minimize forestry impacts: To help address non-tidal wetland habitat loss and fragmentation, there are many ways to potentially improve forestry practices. Areas that have already been heavily timbered should have restored hydrology and be allowed to regrow to return to their natural state, and future clear-cutting in forested wetlands should be avoided. Best management practices (BMPs) that are already in place for forestry operations should continue, such as not harvesting in very wet soils and using tires that minimize soil rutting and compaction.
Beneficial use of dredge material to increase tidal marsh elevation.

Learn More

If you want to get into the weeds and know all the details, you can see the full Inland Bays Wetland Restoration Strategy, now publicly available! Spoiler alert: the full report contains information not only about tidal and non-tidal wetlands, but also about submerged aquatic vegetation (SAV) in the Inland Bays, including widespread problems faced by SAV and tactics to address those issues. You can also explore maps showing potential wetland and SAV restoration areas on public, protected lands in the full report, such as the one shown here. Restoration maps presented in the strategy combined spatial data from the Delaware Watershed Resources Registry (WRR) with other existing spatial data, including current wetlands, highly suitable marsh migration lands, areas containing P. australis, and poorly drained agricultural or rangelands.

Prime non-tidal wetland restoration opportunities in Little Assawoman Bay, circled in light blue.

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uncategorized

Coastal Wetlands: More Than Just a Pretty View

Written on: May 25th, 2022 in Outreach

By Olivia McDonald, Wetland Monitoring and Assessment Program

As you drive through the coastlines of Delaware and roll down your windows, you’re greeted by a view like no other. You spot an expansive marsh on your right, opening to a vast bay filled with boats and glistening with sunshine. Most of us know that feeling – you’ve made it to the coast. But let’s take a look beyond the beauty. Past your binoculars and deep within a coastal wetland habitat that is hard at work. 

According the to Environmental Protection Agency (EPA), “Coastal wetlands include saltwater and freshwater wetlands located within coastal watersheds – specifically, USGS 8-digit hydrologic unit watersheds which drain into the Atlantic Ocean, Pacific Ocean, or Gulf of Mexico.” These land areas are permanently or seasonally inundated with fresh, brackish, or saline water. The plant community contains a variety of species that are uniquely adapted to the degree of inundation, the type of water that is present, and the soil conditions.

Map 1. United States map of the different coastal watershed provinces and their geographic limits. (Credit: Environmental Protection Agency)

Don’t let the word “coastal” trip you up too much. In this case, we’re talking about wetlands that can be tidal and non-tidal, and freshwater or saltwater. Types of coastal wetlands include, marshes, salt marshes, seagrass beds, freshwater marshes, swamps, bottomland hardwood swamps, and mangrove swamps and forests. What is clear from Map 1 is that coastal wetlands can in fact extend many miles inland from the edge of the coast. Each wetland’s condition within the watershed depends on the influences and health of the surrounding watershed. Some of these areas are not small in nature, and can impact large portions of one or more states. 

So what’s the big deal?

To understand the value of coastal wetlands, we need to understand the benefits. Ecosystem services can help us quantify those benefits that these habitats provide and show us how they impact our everyday lives. Let’s take a look at these essential services to people and the environment. 

Clean Water

Ah, nature’s water purification system. Coastal wetlands, and really wetlands of all kinds, filter sediment and absorb pollution from outside influences. Runoff from hard surfaces, being a leading cause of pollution, is combated head-on through wetlands. Extra nutrients and pesticides contributed by development and agriculture are filtered out so they don’t enter local waterways. Wetlands simply trap and filter these impurities, helping maintain healthy waters.

Flood or Storm Protection and Erosion Control

If you live in Delaware, you’re going to really appreciate this one. Coastal wetlands are the first line of defensive during storms or floods for residential and commercial property. By holding back amounts of floodwaters and slowing the rate that water enters a system, wetlands can reduce the severity of negative impacts from severe weather events. Coastal wetlands can also prevent coastline erosion due to their ability to absorb destructive wave energy. Being able to dissipate energy created by ocean waves or water movement helps to slow the degradation of a shoreline. For the first state this means protecting people, land, infrastructure, and agriculture from devastating damages.  

Bowers Beach flooding in May of 2022, Bowers, Delaware.

Carbon Sequestration

As the effects of climate change increase, the need to remove greenhouse gases from the atmosphere becomes more vital for our planet’s future. Certain coastal wetlands, such as salt marshes and seagrass beds, play an important role in decreasing that release. It’s a term we call coastal blue carbon – carbon dioxide that is absorbed and stored in specific coastal ecosystems. These habitats capture and store the gas from the atmosphere in both plants and soil, and even sequester more carbon dioxide than they release. Though the science behind it all is intense, the results can be more simply understood. Coastal wetland ecosystems have a natural ability to reduce the effects of climate change.

Recreation and Tourism

Each coastal wetland is distinct in the habitat it provides, and those areas aren’t just for wildlife. Wetlands provide the public and landowners alike a myriad of opportunities for recreation. From bird watching to hunting, hiking to photography, these ecosystems open the door for people to experience nature. The ever-growing tourist industry centered around Delaware’s beaches do more than just trickle down to hotels, restaurants, and local businesses. With an intricate coastline stretching the length of the entire state, impacts from growth are being seen throughout all three counties. Our coastal habitats are a major economic drivers for a variety of communities job growth and revenue.

Sustainable Fisheries

Imagine your favorite seafood dish. Where do you think it comes from? Many kinds of fish – from salmon to striped bass, as well as lobster, shrimp, oysters and crabs – depend on coastal wetlands for places to feed, live, or reproduce. These areas are like nurseries for young commercial fish and shellfish species. What you see swimming as a little guppy in the back bays may in fact become a 15 pound Bluefish. Quantity and quality of species equals health and extent of wetlands.

Juvenile Mackerel in Millsboro, Delaware.

Loop back around to Map 1 again and zoom into Delaware. The entire state (yes, the whole thing) is zoned as a coastal watershed. So all the wetlands within the 45 watersheds in Delaware are considered to be in coastal watersheds whether they are tidal or non-tidal. Due to their proximity and zonation, these particular wetlands are more at threat than others in the country, making them particularly important for protection.

Once a habitat is degraded or lost, it loses its value and can become costly to recover the benefits it provides. Using scientific research and extensive management can provide an assortment of recommendations to conserve or preserve these coastal ecosystems for the future. Projects and funding across the country are coming to fruition for wetland restoration involving local, state, and non-government organizations. But some of the most influential adaptations start with you. Understanding the functionality of these coastal ecosystems is a large step in the right direction. So next time you snap that photo of a sunset, or take a bite into a fried clam at your favorite restaurant, be sure to thank coastal wetlands; habitats too valuable to lose.

 

Sunset in Lewes, Delaware

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wetland-assessments

A Summer Exploring the Brandywine

Written on: May 25th, 2022 in Wetland Assessments

By Alison Rogerson, Wetland Monitoring and Assessment Program

The summer of 2019 was like most for the Wetland Monitoring and Assessment Program field crew. Similar to summers before it since 2000, we had a selected watershed to focus on and call ‘office’ for the growing season. Field crews spend the summer visiting randomly selected wetland sites, ranging all types, located on public as well as private property. Our job includes trekking to each selected site and conducting a wetland health assessment; a checklist of wetland stressors that allows biologists to rate how well a wetland is functioning. Each site gets rolled together to produce an overall watershed grade which allows DNREC to rate and track how healthy and functioning Delaware’s wetlands are.

Exploring a nice forested riverine wetland site.

The Brandywine River watershed’s Delaware portion stretches from the Christina River to the Pennsylvania state line all the way across the arc- from the Delaware River to the notch. It includes some beautiful landscape but also a lot of highly developed land. Plus signs of topography! Coming from Dover, it was a change of scenery to have boulders and hills. We replaced the tidal wetlands of the coastal plain with groundwater seeps of the piedmont, and it made for an interesting summer- if you are a wetland geek, I guess, which I am.

We spent three hot months exploring the Brandywine watershed, navigating narrow windy roads with absolutely no shoulder, and scrambling up and down steep banks to finally assess 68 wetlands in total. The data we collected was used to rate the health of all wetlands watershed wide – which includes about 2,800 acres. All in all, wetlands in the Brandywine watershed earned a C+ grade. Not the worst but not the best. Here’s more on why they didn’t make the honor roll and how we can make improvements.

The healthiest wetland types were headwater forest flats and groundwater seeps, both earning a B-. Floodplain riverine and isolated depressions both earned C’s. Each wetland type was different in why they received their grade. Flats had excellent habitat quality but poor buffer quality due to development. Groundwater seeps had excellent hydrology but very poor buffer quality due to development. Riverine wetlands had good habitat and hydrology but poor buffer quality. Lastly, depressions had excellent hydrology but very poor buffer quality. All of this is captured colorfully on the Brandywine watershed report card.

An open, wet meadow wetland. Note the proximity to lawn and house.

Any good student would want to bring their grades up after mid-terms, so what can we do to improve wetland health? For all four wetland types, the category with the poorest condition rating was the wetland buffer, or area immediately surrounding. We can’t take away development that is already there but we can do things to protect wetlands and waterways from as many present and future impacts. Presently, landowners can maximize the protection buffers offer by planting more and mowing less- create a wide (50ft), thick vegetated area between yards or roads and wet areas. In the future, we need development to plan for a wide riparian buffer around wetlands and streams. This allows harmful chemicals and nutrients to be filtered out before reaching our waterways. It also provides rich and important plant and wildlife habitat.

For the full watershed health report visit: https://documents.dnrec.delaware.gov/Watershed/Wetlands/Assessments/Brandywine-Watershed-Condition-Report.pdf

 


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