Louisiana Waterthrush (Parkesia Motacilla) Christopher N

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Louisiana Waterthrush (Parkesia Motacilla) Christopher N Louisiana Waterthrush (Parkesia motacilla) Christopher N. Hull Keweenaw Co., MI 4/6/2008 © Mike Shupe (Click to view a comparison of Atlas I to II) This fascinating southern waterthrush sings its loud, clear, distinctive song over the sound of The species is considered area-sensitive babbling brooks as far north as eastern (Cutright 2006), and large, continuous tracts of Nebraska, lower Michigan, southern Ontario, mature forest, tens to hundreds of acres in size, and New England, and as far south as eastern are required (Eaton 1958, Eaton 1988, Peterjohn Texas, central Louisiana, and northern Florida. and Rice 1991, Robinson 1995, Kleen 2004, It winters from Mexico and southern Florida Cutright 2006, McCracken 2007, Rosenberg south to Central America, northern South 2008). Territories are linear, following America, and the West Indies. (AOU 1983, continuously-forested stream habitat, and range Robinson 1995). 188-1,200 m in length (Eaton 1958, Craig 1981, Robinson 1990, Robinson 1995). Hubbard (1971) suggested that the Louisiana Waterthrush evolved while isolated in the Distribution southern Appalachians during an interglacial Using the newer findings above, which were period of the Pleistocene. It prefers lotic derived using modern knowledge and (flowing-water) upland deciduous forest techniques, the "logical imperative" approach of habitats, for which it exhibits a degree of Brewer (1991) would lead us to predict that the morphological and behavioral specialization Louisiana would have been historically (Barrows 1912, Bent 1953, Craig 1984, Craig distributed throughout the SLP to the tension 1985, Craig 1987). Specifically, the Louisiana zone, and likely beyond somewhat, in suitable Waterthrush avoids moderate and large streams, habitat. The Louisiana probably ranged at least selecting small, fast-flowing, first-order streams somewhat into the NLP, and potentially even with gravel bottoms in hilly, upland deciduous the UP, since its range in New England reaches forest (Mengel 1965, Graber et al. 1983, Eaton the latitude of the Keweenaw Peninsula 1988, Peterjohn and Rice 1991, Robinson 1995, (Robinson 1995), and habitats occupied in the Bruner 1998, Cutright 2006, McCracken 2007, northernmost portions of its range often contain Rosenberg 2008). It may nest in swamps and significant coniferous components (Cutright bottomlands without gravel substrates, but less 2006, McCracken 2007, Rosenberg 2008). commonly (Bruner 1998, Kleen 2004, Unfortunately, the statewide deforestation McCracken 2007, Rosenberg 2008), and in brought about by lumbering and settlement lower densities (Graber et al. 1983). preceded ornithologists’ ability to reliably © 2011 Kalamazoo Nature Center Louisiana Waterthrush (Parkesia motacilla) Christopher N. Hull identify this species and accurately define its the species' presettlement range, rather than an habitat (Sager 1839, Gibbs 1879, Cook 1893, expansion of it. Ridgway 1902, Barrows 1912, Wood 1951, Zimmerman and Van Tyne 1959, Brewer 1991). Breeding Biology The Louisiana Waterthrush is among the first of However, even after deforestation had taken the warblers to return in the spring, as well as place, both Cook (1893) and Barrows (1912) one of the first to nest, and has been recorded as considered the Louisiana Waterthrush to be early as 28 March (Kelley 1983). This may be common throughout the SLP, but found an adaptation to the species' habit of nesting in nowhere north of Saginaw or Montcalm and along streambanks, since nests are Counties. In 1936, it was found slightly further vulnerable to flooding (Kleen 2004), and early north, in Newaygo County. (Wood 1951). arrival allows the birds to conduct nest site Declines were reported for the western selection when stream flows are at or near their (Zimmerman and Van Tyne 1959) and then seasonal maxima (Bruce and Peterjohn 1991, eastern (Kelley 1978) SLP, and finally Payne Bruner 1998, Cutright 2006), thus reducing the (1983) reported that the species had become risk of a later nest loss due to flooding. This uncommon and local in the SLP. may also be one of the advantages of selecting small streams, where flood peaks and flow Similar to MBBA I (Hull 1991), MBBA II data volumes are lower than for larger streams (C. (see map) show the Louisiana Waterthrush Hull, pers. obs.). Most nesting occurs from late today to be sparsely distributed in a V-shaped May to mid-June, but a few nests have been pattern which extends northward up the western found during the first two weeks of July (Kelley third of the SLP and into the west side of the 1978, Schumacher 1983). Nests are situated in NLP as far north as Manistee County (just west a hollow or cavity in a stream- or ravine- bank, of the adjacent Wexford County northern limit or in a root mass or stump of an overturned tree of MBBA I); and northward up the eastern third (Barrows 1912, Wood 1951, Bent 1953, of the SLP, into the Thumb as far north as Robinson 1995). Data from Eaton (1958) and Tuscola County (same county and townships as Robinson (1995) suggest that pairs may favor in MBBA I). As in MBBA I, the species was south-facing slopes for nest sites. Clutch size largely unrecorded in the central SLP, most of ranges from four to six, and typically five. Only the NLP, and the entire UP. Also as in MBBA one brood is raised. Louisiana’s are frequently I, the species was reported in far fewer blocks in parasitized by cowbirds, and suffer significant the east than in the west. Generally, there was losses, especially where forest cover is reduced close correspondence with locations for which (Wood 1951, Bent 1953, Eaton 1958, Robinson the species was reported in MBBA I. Many of 1995). the townships in which the species had been detected in MBBA I revealed it again in MBBA Abundance and Population Trends II; quite a number did not, and for far fewer, In MBBA I, the Louisiana Waterthrush was MBBA II revealed new locations. The Wexford reported in 86 blocks statewide: 12 NLP and 74 and Manistee Counties locations are two tiers of SLP (Hull 1991). In MBBA II, it was reported counties north of Wood's (1951) northernmost in 52 blocks statewide: 11 NLP and 41 SLP. breeding record from 1936, and three tiers north This amounts to a decrease in blocks of 40% of the records known by Barrows (1912). statewide: 8% in the NLP, and 45% in the SLP, Thus, the Louisiana Waterthrush has extended between MBBA I and MBBA II. If these its range northward over the past 100 years; figures are adjusted by estimates of reduced however, this is most likely a reoccupation of Atlas effort in these two regions (13.6% in the © 2011 Kalamazoo Nature Center Louisiana Waterthrush (Parkesia motacilla) Christopher N. Hull NLP, and 9.3% in the SLP), the Louisiana compelling reason for the decline of the species Waterthrush may have experienced a 5% in Michigan, particularly in the SLP; and it may increase in number of blocks in the NLP; but it explain why the species appears to be holding seems clear that it suffered a substantial decline its own, or even slightly increasing, in the NLP in the SLP (36%, adjusted), and a visual – where there is overall lower development examination of the map reveals that the greatest pressure. The timing of the species' decline in decline occurred in the west, where a large the SLP, decades after the lumbering era, but number of MBBA I blocks did not yield the bird coincident with increasing development, would in MBBA II. seem to support this conclusion, as would the relative abundance of the Northern Waterthrush The Louisiana Waterthrush's early nesting (which is less demanding of continuous forest season, local distribution, and habitat cover, and is more of a wetland generalist) in preferences are not conducive to roadside the SLP (Hull 2010). The Louisiana detection on BBS routes. As in MBBA I, only Waterthrush, with its narrower ecological three BBS routes reported the species amplitude, is more vulnerable to habitat (compared with 61 for all of FWS Region 3, degradation and loss. with a regional abundance of < 1.0 birds per route). While the Region 3 BBS trend analysis Conservation Needs for 1983-2007 (Sauer et al. 2008) shows a Nationally, the Louisiana Waterthrush is not a general increase in birds per route from 0.15 in species of concern. It is not listed on the U.S. 1983 to over 0.25 in 2007, this was not Watchlist of Birds of Conservation Concern statistically significant, due to the overall low (NAS 2010, ABC 2010), and the IUCN Red List abundance and small sample size. lists it as a species of Least Concern (IUCN 2010). However, significant declines have been The vast deforestation of the logging era, and reported in Ontario, due to forest and wetland concomitant stream degradation due to erosion, loss (McCracken 2007); and in New York, for siltation, and transportation of sawlogs probably unknown reasons, though loss of forest cover resulted in substantial population reductions for due to exotic pests, food loss due to stream this species. Stream damage from the lumber acidification, and high mercury levels are all era, in the form of erosional sedimentation postulated (Rosenberg 2008). (which imbeds essential invertebrate substrates) and increased flood peaks and "flashiness" As a result of the findings of MBBA I (Hull (which endangers nests), remains today in many 1991), the Louisiana Waterthrush is designated streams, and continues to degrade habitat as a species of Special Concern in Michigan quality and reduce wildlife (USDA 1986, (Gibson 2007). The marked decline in records Fitzpatrick et al. 1999, Fitzpatrick and Knox for the species in MBBA II, particularly in the 2000, Riedel et al. 2001, Anderson et al. 2006). SLP, is a cause for concern. Modern-day forestry and development of all types continue to contribute these prevalent To maintain stable, sustainable populations in nonpoint source impacts to streams (USEPA Michigan, the Louisiana Waterthrush requires 1996, MDNR and MDEQ 2009).
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