Quail Hatch Report

Quail Hatch Report

High Male Incubation Good Sign for Fall Bobwhite Abundance

Quail chicks leaving nestThe quail hatch is shaping up to be a good one! Plenty of adult bobwhites and broods are being observed and reported across the Red Hills and Albany area quail properties, as well as our study sites on central Florida Ranches, the Carolinas and Alabama. Breeding season adult survival has been excellent in the Albany area, the Carolinas and central Florida, but average to slightly below average in the Red Hills region. On all of our study sites along the east Coast, we have been seeing average to above average production compared to our historical records. In the Albany area, nest production per capita is well above average, whereas brood production per capita is slightly below average, supposedly due to high attrition from snakes. On all of our other sites (in the Carolinas, central Florida and the Red Hills), nest and brood production has been about average at the mid-season point, but good breeding season survival on all sites, with the exception of our Red Hills study sites, affords a lot of opportunity for birds to re-nest and/or hatch second broods.

Despite average production, poorly timed rains resulted in high amounts of chick mortality in the Red Hills during the first (late May, early June) wave of hatches, but chick survival has dramatically improved since then. However, high snake activity has resulted in higher than usual chick mortality to snakes, compared to the past couple of years. The good news is that there still appears to be a lot of cotton rats out there to alleviate the pressure on the young quail chicks. In fact, on our Albany area study sites, we recorded an all-time high abundance of cotton rats during our early August sampling period.

Beyond chick survival and our typical per capita production tracking metrics (broods and nests produced per hen), male incubation rates are excellent so far at >27% for Tall Timbers and Dixie study sites which is already at our long-term average for the entire breeding season. Our recent research has shown that male incubation patterns are 2.5 times more predictive of population change than any other bobwhite demographic we monitor. As a result, when male incubation rates are above average, we are 78% more likely to observe a population increase, compared to years when male incubation rates are lower than 28%. During years when male incubation is higher than normal, overall production from hens can be biased low or underestimated, which appears to be the case this year. An even greater predictor of population growth is broods hatched by males. To date, the number of broods hatched by males is 0.16 for the breeding season. Our long-term data on Tall Timbers indicates that when broods produced per male is at or greater than 0.16, a population increase was observed nearly 88% of the time (see Figure 1). If this pattern is holds true for this year, we could see modest increases in fall bobwhite abundance.  Taken collectively, there is reason for optimism heading toward the breeding season finish line. A good late hatch will be the deciding factor for many as to whether population increases are observed this fall compared to last year.

Figure 1. Bobwhite density (and lambda – population growth rate) and reproduction of Northern Bobwhite at Tall Timbers from 2000 – 2019. Gray bars represent bobwhite density (birds per acre) and solid black line lambda; the dotted-black line represents successful male-incubated nests per radio-tagged male (broods per male), and the dashed-grey line represents successful female-incubated nests per radio-tagged female (broods per female).

 

Raptors and Bobwhite Survival

Raptors and Bobwhite Survival

Impacts of Raptor Abundance on Bobwhite Survival

For more than a decade (2008–2020), the Tall Timbers Game Bird Program has collected raptor count data on two Red Hills properties and one Albany area Plantation in attempt to capture spatial and temporal patterns in raptor abundance as it relates to bobwhite demographics. In April, Justin Rectenwald successfully defended his thesis earning a Master’s degree at The University of Georgia using this long-term dataset where he evaluated “The Effects of Variation in Raptor Abundance on Northern Bobwhite Survival.” He is now employed full-time as a Game Bird Biologist with the Albany Quail Project. As with any good research, we were able to corroborate a few “prior beliefs,” quell some others, and ask some new questions. In this summer’s edition of the Quail Call newsletter, we will recap our findings, but here are a few key take home points from Justin’s thesis:

Raptor abundance varied throughout the year with the timing of regional pulses varying by species group.

Accipiters (e.g., Cooper’s hawks), buteos (e.g., red-tailed hawks), and owls exhibited different abundance patterns seasonally and annually both within and among species. These fluctuations in raptor numbers were largely associated with natural migration for accipiters and buteos and dispersal of juvenile owls. The bulk of regional and temporal variation in raptor pulses was during the bobwhite non-breeding season, whereas raptor fluctuations during the bobwhite breeding season (May–September) remained relatively constant and similar for each raptor group. Whereas a latitudinal effect was not observed in our data, differences did exist among sites, indicating that variation in raptor numbers observed may be related to differences in resource availability (i.e., presence/absence of hardwood drains or amount of hardwoods in uplands).

Minor pulses in raptor numbers can negatively impact bobwhite survival.

Bobwhite were more vulnerable to buteo and owl depredation during breeding season due to reduced vigilance of mating activity by bobwhite, as well as nest-building and egg-laying, incubation, and brood rearing activities. An increase in buteo and accipiter abundance was observed in the late summer and fall resulting in declines in annual bobwhite survival. In particular, as previously thought, accipiters have a negative influence on bobwhite survival in late winter, which is associated with an increase in accipiter abundance coupled with deterioration of cover conditions late in the hunting season.

Owls appear to have a larger impact on bobwhite survival, especially during the breeding season, than previously thought.

A somewhat novel or surprising finding from this research was that owls influenced survival at a higher rate than expected. The data suggest that for each additional owl added per 82 acres, bobwhite survival decreased by nearly 3.5 times. As is also true for accipiters, this effect was much larger than that observed for changes in buteo density, but there are also more buteos, as a whole, on the landscape. It appears that a greater proportion of barred owls exist on the landscape in the Red Hills region, compared to a greater number of great-horned owls in the Albany area. While great-horned and barred owls are sympatric species, there is a high amount of competition among these owls, which may impact bobwhite survival by impacting species-specific owl abundance in the uplands.

Although avian predators are federally protected, we can moderate their impact on bobwhite mortality rates by implementing sound management practices to reduce both the amount of raptor habitat in the uplands, and increasing the quality of vegetation conditions, as well as employing additional practices, such as supplemental feeding to reduce bobwhite foraging times. This research indicated that the major pulses of avian predators due to migration in late winter and early spring is over in the Southeast by late February and early March, but this is also a moving window related to weather conditions. For example, cold winters may delay Accipiter migration timing, which could dramatically decrease monthly bobwhite survival during late winter and impact bobwhite breeding densities. Similarly, cotton rat survival and abundance may also be influenced by these same pulses in raptor abundance. Importantly, this study demonstrates that during most years when a proper burn program is implemented (small scale burning, and distributing burns properly during March–May), raptor impacts on bobwhite survival can be mitigated, but large scale burning or burning too much at one time may have negative impacts on the bobwhite population. Going forward we plan to take a closer look at northerly spring migration patterns and how they are affected by weather, as well as how habitat modifications (i.e. hardwood removal, thinning mid rotation pines, snag removal) may impact raptor numbers on a site.

Nuthatch Population Reintroductions

Nuthatch Population Reintroductions

Population Reintroduction of Brown-headed Nuthatch Provides New Information

Population reintroductions are increasingly important for managing rare wildlife. Habitat loss and fragmentation will only increase over the coming decades, meaning that space for wildlife will increasingly be smaller and dissected more frequently by roads, urbanization, and unsuitable habitats. These changes especially pose threats to species that need large areas to survive or have specialized habitat needs.

Jim Cox uses a recording of a Brown-headed Nuthatch call to lure birds to catch in the mist net set up nearby. Photo by William Eaton

Population reintroductions also regularly provide new information on the species involved, as some of our recent work has shown. The Stoddard Bird Lab collaborated with Gary Slater (Center for Natural Lands Management, Washington) to look at the development of cooperative breeding in two reintroduced populations of the Brown-headed Nuthatch. Cooperation in the nuthatch occurs when adult males decide to forego their chances to breed and instead assist in the breeding efforts of another male and his partner.

It’s an unusual type of behavior (found in <5% of all songbirds), and previous work with a bird that breeds cooperatively suggested cooperation occurred only after the available habitat on the reintroduction site had become saturated. Before that time, the excess breeders moved into a surrounding landscape devoid of other males to set up territories and attempt to secure mates, rather than assist in the breeding efforts of others.

Gary reintroduced nuthatches to the Everglades National Park in the late 1990s and monitored the growth of the population for five years. More recently, we reintroduced nuthatches to Jonathan Dickinson State Park and have monitored birds there for two breeding seasons. In both cases, cooperation occurred in the first couple of breeding seasons following the initial releases, well before the available habitat (over 9,000 acres on both sites) was saturated.

The results provide novel support for factors other than lack of space in driving cooperative behavior. Rather than habitat saturation, factors such as the number of males and females available appear to play a bigger role. When there is an excess of males, some males elect to help others rather than set up and defend a lonely territory.

Our work on Jonathan Dickinson has also yielded other novelties. The Brown-headed Nuthatch is thought to be a sedentary species that sets up shop in a small area (about 10-15 acres), and then spends the rest of its life in the general vicinity. Some of the individuals we’ve monitored on Tall Timbers have not moved more than 300 yards in the 10 years they’ve been alive! In contrast, we’ve seen some drastic movements in the first two breeding seasons in our reintroduced population. The two nesting pairs we had the first year post reintroduction have moved over a mile to new nesting locations in 2020. There were no other territorial nuthatches on the park back in 2019, and the lack of neighbors allowed the birds to roam over several hundred acres (not the more typical 15 acres). The changes point to the role that neighbors might have when most individuals in a population try to find breeding habitat, not simply physical features such as food resources and the maturity of pines..

A nesting pair of nuthatches reintroduced to Jonathan Dickinson State Park in 2019 that has moved over a mile to a new nesting location in 2020. Photo by William Eaton

This work also has important conservation implications, in addition to some of the theoretical elements discussed above. The nuthatch has disappeared from many areas in south Florida, including several large (5000+ acres) tracts of public land. The populations remaining in south Florida have lowered genetic diversity, which may be a product of the inability for individuals to move regularly among increasingly isolated patches. Tools like reintroduction and translocation are likely to be increasingly needed to combat these threats, as habitat loss and climate change continue to alter the existing landscape.

Movements of a male color-marked nuthatch reintroduced to Jonathan Dickinson State Park in 2018. The area extends over nearly 200 acres, 10x the normal area used. Red crosses show nesting locations for this male and his mate in 2019 (northern most) and 2020 (southwest).

 

Plant Responses to Fire

Plant Responses to Fire

First glimpses into plant responses to fire
reintroduction

Last fall we began a study aimed at monitoring the response of vegetation to reintroduction of fire into pine communities where fire had been excluded for several decades. Our hypothesis was that several plant species survive extended fire exclusion as living roots, even while invisible above ground, then resprout following fire re-introduction. We set up pre-burn plots at six sites; four of them were burned early this year: Plank Road State Forest, FSU Gulf Coastal and Marine Lab, St. Joseph Buffer Preserve, and a mountain longleaf site near Weogufka, Alabama.

Each of the burns appear to have accomplished the tricky objective of top-killing the overgrown broadleaf woody vegetation, while not consuming much of the accumulated duff, which can be especially lethal at the bases of pine trees. The pines still look healthy, but we will hold judgement until they survive their first year.

The vegetation response so far has been subtle but interesting. As expected, most of the woody plants that were top-killed have resprouted, although many have not. Some new plants have emerged, and most of them have resprouted from roots or tubers. Among the species that were previously not seen during our thorough pre-burn censuses, but re-emerged from roots or tubers are bracken fern (Pteridium aquilinum), Atlantic pigeon wings (Clitoria americana), and greenbriars (Smilax auriciulata and S. rotundifolia). Several other species not previously seen were found post-fire, but they showed evidence of having above-ground vegetation pre-fire, typically a small burn stem. This suggests that some plants, while not completely subterranean during fire exclusion, had greatly reduced above-ground vegetation to the point of being practically invisible.

Bracken fern emerging following fire at the St. Joseph Buffer Preserve in a plot where it was not seen before the fire.

Also new to the plots were many seedlings, especially at the Weogufka site, some of which were likely in the soil before the fire, and others that may have dispersed to the site following the fire. These plants included various witchgrasses (Dichanthelium) and goldenrods (Solidago), as well as tree species including red maple (Acer rubrum), tulip poplar (Liriodendron tulipifera), sassafras (Sassafras albidum), and some oaks (Quercus).

Post-burn plot at mountain longleaf site near Weogufka, Alabama.

As the duff continues to be reduced toward the natural condition of exposed mineral soil, there may be more plants that emerge. In any case, we are poised to learn a great deal about pine community recovery after fire exclusion and reintroduction.

Bobwhite Hunting Report

Bobwhite Hunting Report

Excellent bobwhite hunting reported and a favorable forecast for breeding

Despite not having a good late hatch last breeding season, quail hunting has been exceptional. Reports from several managers in the Red Hills region and Albany area indicate that bird numbers are up 5–10%, with some properties being up as much as 45% in terms of coveys moved per hour. In central Florida and the Carolinas, our study sites also indicate similar good fortune with bird numbers being up >45% on each property being monitored via radio-telemetry. We believe the good bird numbers in the fall along the east Coast are in large part due to excellent chick survival during the 2019 breeding season, resulting in an increase of first-year birds being recruited to the hunting season. This has been substantiated by harvest ratios averaging 75-80% for first-year (juvenile) birds.

Overwinter survival is about average through February on 2 of 3 properties we are monitoring in the Red Hills (62% and 48% at Tall Timbers and Dixie Plantation, respectively), and Albany region (>60%). During our January quail trapping season, we continued to observe high cotton rat numbers, and given the relatively mild winter, we are optimistic for a good carryover of cotton rats, as well as a good carryover of bobwhite to the 2020 breeding season, setting the stage nicely for the upcoming breeding season. However, the same mild conditions profiting cotton rats has apparently affected raptor migration patterns as well, especially Buteos (red-tailed hawks and red-shouldered hawks).

During December, we observed higher overall raptors numbers (see Figure 1– Fall Raptor Counts), especially Butoes, such that migrating hawks stayed in the region longer than usual, likely due to the warm conditions early and presence of a healthy prey base. Contrary to higher Buteo numbers, Accipiter abundance ( e. g. Cooper’s Hawks) has been lower than typical throughout the fall and winter, so far, likely offsetting higher mortality associated with Buteos. The cooler weather observed in January finally compelled many raptors to move farther south; they have not yet begun to migrate back north, resulting in lower than average numbers during the late winter (Jan and Feb) months so far, as indicated by our weekly raptor counts (see Figure 2). Typically, when raptor numbers are lower than normal in January and February, they are higher than normal in March and April. As such, careful consideration to management during the burning season will help to reduce the most important pinch point of the year for bobwhite—the inextricable interaction of burning, bobwhite covey break-up and raptor migration. In addition to broadcast supplemental feeding in good habitat areas, we recommend burning at small scales and distributing timing of burns throughout March, April, and May. This should facilitate keeping as much cover for as long as possible and mediate predation risk of bobwhite until the raptor migration back north is over.

Figure 1

Figure 2