2012). Previous studies on the movements of Hector’s dolphins suggest that individuals are not likely to regularly move across distances larger than approximately 60 km, with only rare movements in excess of 100 km (Bräger et al. 2002, Stone et al. 2005, Rayment et al. 2009). This limited movement is consistent with the limited gene flow observed within the Hector’s dolphin subspecies, among the East Coast, West Coast, and southern Te Waewae Bay and Toetoe

Bay populations (Fig. 1; Hamner et al. 2012). Genetic monitoring provides a framework for assessing changes in the demographic and genetic status of a species by establishing a baseline genetic assessment from an initial sampling event, followed by the continued collection and analysis of samples Selleck Sirolimus over time (Schwartz et al. 2007). Here we report the unexpected natural dispersal of Dabrafenib four Hector’s dolphins detected between 2010 and 2012 through the genetic monitoring of the Maui’s dolphin along the northwest coast of the North Island (Oremus et al. 2012). We also report two additional Hector’s dolphins that were sampled in 2005 and 2009 on the southwest coast of the North Island, outside the known distributions of either subspecies.

The northward dispersal of Hector’s dolphins into the distribution of the Maui’s dolphin could lead to the genetic enhancement of Maui’s dolphins and promote the preservation of the species as part of the west coast

North Island marine ecosystem. As part of an on-going collaborative program for monitoring the abundance and genetic diversity of Maui’s dolphins, small skin samples were collected via dart biopsy (Krützen et al. 2002) during boat-based surveys conducted from 4 February to 2 March 2010 and from 14 February to 10 March 2011 (Fig. 1; see Oremus et al. 2012). Additionally, a dart biopsy sample collected from a single dolphin sighted in Wellington Harbour in 2009, and skin samples collected from all Maui’s or Etofibrate Hector’s dolphins recovered as beachcast or entangled carcasses through 25 April 2012 were provided to us by the New Zealand Department of Conservation and archived in the New Zealand Cetacean Tissue Archive at the University of Auckland (Thompson et al. 2013). All samples were stored in 70% ethanol at −20°C prior to tissue digestion with proteinase K followed by total cellular DNA extraction using a standard phenol:chloroform protocol (Sambrook et al. 1989) as modified for small samples by Baker et al. (1994). We assembled DNA profiles for each sample, including genetic sex identification, mtDNA control region haplotype and 21-locus microsatellite genotypes. Existing DNA profiles previously reported for the Maui’s dolphin baseline samples collected in 2001–2007 (Baker et al., in press) and for the samples collected in 2010–2011 (Oremus et al. 2012) were built upon to complete the extended DNA profiles described here.