Abstract. Monthly changes in the community structure of hypoxic soft‐bottom macrobenthos have been studied at a station at 34 m depth in Ancón Bay (Peru) before and during two El Niño (EN) events. Of these events, 1982‐83 is considered the strongest, and 1991–93 one of the most prolonged in the 20th century. On the oceanographic scale, EN 1982–83 ranges as “very strong”, whereas EN 1991–93 ranges as “moderate”. The thermal anomalies at the station during EN 1982–83 (+ 7.8 °C) were almost twice those of EN 1991–93 (+ 4.1 °C). However, the community changes were not in all cases proportional to the extent of warming. Species numbers increased in a similar way (up to 24 species from near zero in each of the two events), but maximum faunal density was five times higher, and mean biomass was twice as high in 1982–83 compared with the event a decade later. Species diversity was slightly higher during EN 1982–83, whereas successional and trophic changes occurred on a broader scale during EN 1991–93. On the whole, the impact of the long‐lasting event on the small soft‐bottom macrofauna was not much weaker than that of the exceptionally strong event. The authors discuss the mechanisms which may be responsible for the differences and similarities encountered in the benthic community dynamics during these two events. Both in the unusually strong and the unusually long EN, the community revealed a pattern of early biological response several months ahead of the onset of local warming which marks the official begin of EN. The question is addressed to what extent the increase of certain parameters in the benthic community could be used for predictive purposes.

Se reporta el hallazgo de moluscos cuya distribución conocida se encuentra dentro de los límites de la Provin cia Panameña, en diversas localidades de la Provincia Peruana entre los años 1972 y 1994, período en el que se presentaron varios eventos "El Niño". Fue posible determinar 15 especies de moluscos que ampliaron su distribu ción: Pteria sterna, Orobitella peruviana, Cryptomya californica, Cerithíum (T.) stercusmuscarum, Malea ringens, Hexaplex brassica, Thais styl/manberryí, T. (M.) triangularis, T. (T.) cal/aoensís, Acanthina brevidentata, Purpura pansa, Neorapana murícata, Anachis (C.) nigricans, Cancel/aria (C.) decussata y C. (8.) chrysostoma. Se postula una variabilidad en los límites de las provincias biogeográficas de la costa peruana, controlada por el ENSO.