Habitat Restoration and Management: the Power of Volunteering!
The current phase of WCAMP’s Oregon Spotted Frog Project (see below) involves restoring and enhancing key Oregon Spotted Frog (OSF) breeding and tadpole rearing habitats at the Whatcom Land Trust’s Samish River Preserve. Project results indicate that the number of frogs in our study population is declining, particularly in one area (“Southeast Meadow”), where more than half of the frogs breed each year. This decline is evidently related to changes in habitat, exacerbated by dry weather conditions in recent years. The culprit is reed canary-grass, an invasive, tall, densely-growing, wetland grass, which gradually degrades or eliminates sites suitable for egg laying and causes premature drying in aquatic habitats necessary for the survival of tadpoles and young-of-year frogs.
In order to reverse this population decline, we have developed and are implementing a multi-year habitat plan for Southeast Meadow. The plan combines habitat restoration and enhancement. Habitat restoration represents long-term improvements in habitat, primarily by creating deeper pools than would otherwise exist to be used by all Oregon Spotted Frog life stages, but particularly as tadpole habitat. We create these pools by breaking through and removing sections of a floating rooted mat of reed canary-grass that covers water more than two-feet deep. Much like a “quaking bog,” the rooted reed canary-grass is a layer of roots and muck that floats at or near the surface of the water, denying access to the aquatic habitat underneath. We have now completed three new pools – one each year – and the first of these (created in Sept-Oct 2016) has been successfully used by Oregon Spotted Frog tadpoles for the past two years. We are hoping that some of the frogs from the 2017 year class will be returning to breed for the first time in 2019 and 2020.
Habitat enhancement represents shorter-term improvements in habitat, particularly mowing the reed canary-grass in late summer and autumn to prevent thatch build-up and creating open, shallow water areas where Oregon Spotted Frogs can lay their eggs in early spring the following year. We also make pathways for tadpole dispersal. These habitat changes are temporary — much like mowing your lawn does not have a lasting effect. Eventually the reed canary-grass again grows tall and dense, but not before the frogs have benefited from the changes.
Critically, our plans are guided by site-specific data from: (1) water depth monitoring performed since 2016, (2) Oregon Spotted Frog egg mass surveys that we have led since 2013, (3) studies of tadpole growth, development, and abundance at different sites used by Oregon Spotted Frog in 2014, 2016, and 2017, and (4) vegetation monitoring within our habitat work area at Southeast Meadow. Going forward, we will continue to collect these data, and test whether our efforts have been effective and can be sustained. We will also continue to share our methods and results with other scientists and land-managers to conserve the Oregon Spotted Frog and move the species toward recovery.
Since beginning the first pool in September 2016, our volunteer effort has invested hundreds and hundreds of hours of hard, but satisfying work in this project. The habitat transformation at Southeast Meadow envisioned in our plan is slowly taking shape. 2019 promises to be our biggest year, with an expanded project focus to include new habitat restoration techniques and work at additional sites in need of restoration. As always, the story begins and ends with the frogs, who will soon be breeding again and will tell us whether we are on the right track! On behalf of the frogs: “Thank You!” to all the volunteers and our project partners, the Whatcom Land Trust, U.S. Fish and Wildlife Service, Washington Department of Fish and Wildlife, and Wildlife Conservation Trust, for their support. Click on this link for more information and photos showing our progress on this habitat project: Habitat Restoration and Management
Background: WCAMP coordinates with State and Federal wildlife agencies to monitor and research a population of Oregon Spotted Frog (OSF) (Rana pretiosa) at the Whatcom Land Trust’s Samish River Preserve. The information we are collecting may help guide future site management decisions by the Land Trust, and other landowners and agencies working to conserve this rare species elsewhere. WCAMP’s Oregon Spotted Frog monitoring and research project is authorized under a U.S. Fish and Wildlife Service (USFWS) Fish and Wildlife Species Recovery Permit issued to our Lead Scientist, Stephen Nyman. Our projects have successfully competed for grant awards by the USFWS in 2016 and again for 2019. Each of these awards provide a vital portion of the costs of our projects, with the rest from donated time and expenses. With your help, we could do more. If you are interested in participating as a volunteer, making a financial contribution, or learning more about our studies and planned efforts in 2019, and how you can help, please contact Stephen. For much more Oregon Spotted Frog information and photographs, click on this link to the OSF Species Facts page: Oregon Spotted Frog (Rana pretiosa)
Populations of OSF were first discovered in Whatcom and Skagit Counties in 2011 as a result of survey work performed by the Washington Department of Fish and Wildlife and volunteers. Surveys were conducted on private lands (with landholder permission) in the South Fork of the Nooksack River and the headwater region of the Samish River. Egg mass surveys in the first year resulted in the tentative detections of a number of occupied sites, which were subsequently confirmed in 2012 when adult frogs, egg masses, and larvae were all observed. A population has also been discovered in the Sumas River drainage. The OSF population at the Samish River Preserve is the only population which has been surveyed each year since 2012.
Originally found from the Lower Fraser Valley of British Columbia to northeastern California, the OSF is believed to have disappeared from large portions of its former range. The species has been listed as State Endangered since 1997 and federally Threatened under the Endangered Species Act since August 2014. The USFWS is currently working on the federal Species Recovery Plan for OSF.
The OSF is highly aquatic, requiring sites with permanent water, but breeding in areas of shallow water, which may dry seasonally. Egg-laying sites tend to be open and sunny, with sparse, low vegetation when the frogs are breeding. The ability of hatchlings to move from areas that do not hold water for a sufficient period for larval development (3-4 months) to more persistently wet areas is crucial to their survival. The quality of egg-laying and tadpole rearing habitats is degraded in areas where the common, invasive reed canary-grass predominates. Unfortunately for the frogs, all known OSF sites in Washington are affected by reed canary-grass, which thrives in shallow, wet areas and can reach heights of more than 6 feet, excluding other vegetation, and creating a thick layer of submerged thatch.
2014: The 2014 study, approved by the Washington Department of Fish and Wildlife, monitored OSF breeding at the Preserve – recording 364 egg masses (compared to 189 in 2013) – and included a summer of non-lethal sampling (i.e., capture and release) to document OSF tadpole habitat use, growth and development, and other aspects of the population. The Preserve is an ideal site for the study because the OSF population here is relatively large and the habitats used by the species are diverse, including two large ponds and three shallow, grassy wetlands (or “meadows”) with open areas and dense stands of reed canary-grass. Based on their locations, we have named these areas North Pond, South Pond, North Meadow, Southeast Meadow, and Southwest Meadow. In 2014, about 70 percent of the population bred at the meadow areas compared to 30 percent at the ponds. Considerable scientific research has been devoted to OSF; however, the tadpole stage has been largely neglected and many fundamental questions have not been investigated. Questions we are asking include:
- Do OSF eggs and larvae perform equally well in each area (i.e., comparing number and survival of egg masses to hatching; developmental rates, growth, time to metamorphosis, and relative abundance of larvae)?
- What predators occur in each area?
- What habitats are larvae actually using in each area and how far do they disperse from egg masses after hatching?
- Are any of the areas “sink” habitats (i.e., habitats where few or no tadpoles survive to metamorphosis)?
- Could any of these areas be improved with management?
Our results in 2014 provided evidence that conditions for OSF tadpoles were least favorable for growth and development at Southeast Meadow, where more than half of the population typically breeds. Tadpoles grew and developed faster at the ponds; however, the ponds supported predators that did not occur in the meadows, including Giant Water Bug and Brown Water Scorpion.
2015: In 2015, the OSF population at the Samish River Preserve endured drought conditions and an unusually warm summer. Although eggs in most of the 298 documented egg masses hatched, Southeast Meadow (where there were 159 egg masses) was completely dry by June 15, much too early for any tadpoles to have reached metamorphosis. This early drying was probably hastened by the advanced stage of reed canary-grass invasion into deeper water areas that might have otherwise provided tadpole habitat. A similar pattern occurred elsewhere, with North Meadow (15 egg masses) drying on June 28 and Southwest Meadow (21 egg masses) on July 29. If any tadpoles survived to metamorphosis in these areas, the metamorphosed young-of-year would still have had to travel in dry conditions through dense reed canary-grass to reach permanent aquatic habitats after the last pools dried.
The fate of tadpoles at the ponds in 2015 is unknown. Metamorphosed young-of-year OSF were not observed, suggesting that survival was lower than in 2014, possibly due to predation. Nevertheless, the drought illustrated the importance of the ponds in providing summer habitat for adult OSF, when other areas were dry. However, more information is needed regarding seasonal movements within this OSF population and adequacy of aquatic connections to allow the frogs to move between sites, particularly in late summer.
February 26, 2015: WCAMP Lead Scientist, Stephen Nyman, presented two talks and one poster at the most recent meeting of the Society for Northwestern Vertebrate Biology in Portland, Oregon. These summarized the findings from our 2014 field season and were very well received. Way to go, Stephen! Here are the titles of those talks, and feel free to contact Stephen if you want more information:
- Evaluation of characteristics to differentiate larvae of Oregon Spotted Frog and Northern Red-legged Frog.
- Ecological aspects of Oregon Spotted Frog eggs and larvae at ponds and meadows of the Samish River Preserve, Whatcom County, WA
- Evaluation of an aquatic funnel trap for shallow water habitats used by Oregon Spotted Frog (Rana pretiosa) – Poster
Click on this link to view a fresh clutch of Oregon Spotted Frog in Whatcom County. Listen carefully and you can here their distinctive “knock, knock, knock” call (turn up volume to max). Thank you, Stephen Nyman, for sharing this video.
Click on the link below to watch a video on the status of the Oregon Spotted Frog in the Fraser Valley, BC.
Chris Brown (WCAMP volunteer) took this video of a large congregation of Oregon Spotted Frog egg masses. This was shot in mid March 2014.
Get the latest information on the status and management recommendations for the Oregon Spotted Frog. The new Draft Washington State Oregon Spotted Frog Recovery Plan and the results of WDFW surveys for Oregon Spotted frogs in Skagit and Whatcom Counties are out.
Click on the files below to read documents.