The first at-sea estimates of density and abundance of the olive ridley turtle Lepidochelys olivacea in the eastern tropical Pacific (ETP) were produced from shipboard line-transect data. Multi-ship surveys were conducted in 1992, 1998, 1999, 2000, 2003, and 2006 in the area defined by 5°N, 120°W, and 25°N and the coastline of Mexico and Central America. Sighting data of olive ridleys were stratified by survey effort and sighting conditions, thereby reducing potential biases from heterogeneous observation conditions. Dive data from satellite telemetry studies were used to correct for the proportion of turtles that were submerged and unavailable for detection during the surveys. A weighted average of the 5 by-year estimates (1998 to 2006) was 1.39 million (coefficient of variation, CV = 19.7%; approximate 95% CI: 1.15 to 1.62 million). Our findings are consistent with the dramatic increases of olive ridley nesting populations that have been reported over the past decade for beaches in the ETP. : 191-203, 2007 ities (Cheng & Chen 1997, Pandav et al. 1998, Lewison et al. 2004, Pinedo & Polacheck 2004, which are thought to be a significant source of mortality. As a result of these impacts, nesting abundances on many of the primary nesting beaches have declined (Valverde et al. 1998, Shanker et al. 2003 to the extent that several olive ridley arribadas appear to be an endangered phenomenon (Brower & Malcolm 1991). Due to these ongoing threats and ensuing population declines, the olive ridley was officially protected in Mexico in 1990(DOF 1990, and remains listed as 'Endangered' in the IUCN World Conservation Union Red List (IUCN 2006) and included in Appendix I of the Convention on International Trade in Endangered Species (CITES). Despite a worldwide increase in research and conservation of olive ridleys, few data are available on their density and abundance in most regions.
KEY WORDS: Line transect · DISTANCE · Endangered species
Resale or republication not permitted without written consent of the publisherEndang Species Res 3Successful management of a population requires information about mortality, recruitment, and temporal changes in abundance or density. Longitudinal estimates of abundance or density are necessary for management and monitoring of marine turtle populations. For marine turtles, the annual number of females at nesting beaches has been used as an index of abundance (Meylan 1995, Troëng et al. 2004, Kaplan 2005. Because the proportion of the total females nesting in any one season may vary substantially from year to year (Broderick et al. 2001, Shanker et al. 2004, Dutton et al. 2005, inter-annual variability in nesting abundance does not necessarily reflect actual changes in abundance. In the case of olive ridleys, this problem is exacerbated by the difficulty of generating accurate abundance estimates of nesting females during arribada events.An alternative and complementary method to nesting beach surveys is sampling at sea. Transect sampling, such as line-transect and strip-transe...