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The Origin and Development of the CCAP in Zambia 1882-20042
Coertzen, P Chilenje, V1 University of Stellenbosch The origin and development of the CCAP in Zambia 1882-20042 INTRODUCTION For a very long period of time the Church of Central Africa Presbyterian (CCAP) in Zambia had no record of its historical roots. As a result many Zambians questioned the independent existence of this church; others called it a “Malawian” church and others a “break away”. My hypothesis shows that it is clear from history that the CCAP existed among the Zambian people since the 1880’s. In addition it reveals that the CCAP in Zambia traces its roots from the Livingstonia Mission of the Free Church of Scotland which started its work in Central Africa in 1875 (Laws, 1934:7,16). Through this mission the church is known to have grown to a fully fledged denomination. It is also to be noted that the CCAP in Zambia is also a fruit of the activities of CCAP General Synod members in the urban areas. THE LIVINGSTONIA MISSION The Livingstonia Mission of the Free Church of Scotland was formed in memory of the late Dr. David Livingstone who died at Chitambo in Northern Zambia in 1874. Dr. David Livingstone’s famous appeal made at a large meeting in the Senate House at Cambridge on 4 December 1857, his three great journeys in Africa, and his reports on the “Open path for commerce, civilisation and Christianity” evoked a response from a wide variety of people (Johnston 1908:28, 29). Through the Livingstonia Mission of the Free Church of Scotland churches were established in Malawi and Zambia (Laws, 1934:179,185,196). -
Phylogeny of a Rapidly Evolving Clade: the Cichlid Fishes of Lake Malawi
Proc. Natl. Acad. Sci. USA Vol. 96, pp. 5107–5110, April 1999 Evolution Phylogeny of a rapidly evolving clade: The cichlid fishes of Lake Malawi, East Africa (adaptive radiationysexual selectionyspeciationyamplified fragment length polymorphismylineage sorting) R. C. ALBERTSON,J.A.MARKERT,P.D.DANLEY, AND T. D. KOCHER† Department of Zoology and Program in Genetics, University of New Hampshire, Durham, NH 03824 Communicated by John C. Avise, University of Georgia, Athens, GA, March 12, 1999 (received for review December 17, 1998) ABSTRACT Lake Malawi contains a flock of >500 spe- sponsible for speciation, then we expect that sister taxa will cies of cichlid fish that have evolved from a common ancestor frequently differ in color pattern but not morphology. within the last million years. The rapid diversification of this Most attempts to determine the relationships among cichlid group has been attributed to morphological adaptation and to species have used morphological characters, which may be sexual selection, but the relative timing and importance of prone to convergence (8). Molecular sequences normally these mechanisms is not known. A phylogeny of the group provide the independent estimate of phylogeny needed to infer would help identify the role each mechanism has played in the evolutionary mechanisms. The Lake Malawi cichlids, however, evolution of the flock. Previous attempts to reconstruct the are speciating faster than alleles can become fixed within a relationships among these taxa using molecular methods have species (9, 10). The coalescence of mtDNA haplotypes found been frustrated by the persistence of ancestral polymorphisms within populations predates the origin of many species (11). In within species. -
Lake Chala Tilapia (Oreochromis Hunteri) Ecological Risk Screening Summary
Lake Chala Tilapia (Oreochromis hunteri) Ecological Risk Screening Summary U.S. Fish & Wildlife Service, March 2012 Revised, June 2018 Web Version, 12/15/2020 Organism Type: Fish Overall Risk Assessment Category: Uncertain Photo: D. H. Eccles. Licensed under Creative Commons BY-NC 3.0. Available: http://www.fishbase.org/photos/PicturesSummary.php?StartRow=0&ID=2032&what=species&T otRec=2. (June 18, 2018). 1 Native Range and Status in the United States Native Range From Froese and Pauly (2018a): “Africa: endemic to Lake Chala [Seegers et al. 2003].” 1 Status in the United States No records of Oreochromis hunteri in trade or in the wild in the United States were found. The Florida Fish and Wildlife Conservation Commission has listed the tilapia Oreochromis hunteri as a prohibited species. Prohibited nonnative species (FFWCC 2018), "are considered to be dangerous to the ecology and/or the health and welfare of the people of Florida. These species are not allowed to be personally possessed or used for commercial activities. All species in the genus Oreochromis are considered regulated Type A species in Washington. Regulated Type A species (Washington State Senate 2019) are “nonnative aquatic animal species that pose a low to moderate invasive risk that can be managed based on intended use or geographic scope of introduction, have a beneficial use, and are a priority for department-led or department-approved management of the species' beneficial use and invasive risks.” Possession of any species of tilapia is prohibited without permit in the State of Louisiana (Louisiana State Legislature 2019). O. amphimelas falls within Group I of New Mexico’s Department of Game and Fish Director’s Species Importation List (New Mexico Department of Game and Fish 2010). -
Lake Malawi Destination Guide
Lake Malawi Destination Guide Overview of Lake Malawi Occupying a fifth of the country, Lake Malawi is the third largest lake in Africa and home to more fish species than any other lake in the world. Also known as Lake Nyasa, it is often referred to as 'the calendar lake' because it is 365 miles (590km) long and 52 miles (85km) wide. Situated between Malawi, Mozambique and Tanzania, this African Great Lake is about 40,000 years old, a product of the Great Rift Valley fault line. There are fishing villages to be found along the lakeshore where residents catch a range of local fish including chambo, kampango (catfish), lake salmon and tiger fish. The export of fish from the lake contributes significantly to the country's economy, and the delicious chambo, similar to bream, is served in most Malawian eateries. Visitors to Lake Malawi can see colourful mbuna fish in the water, while there are also occasional sightings of crocodiles, hippos, monkeys and African fish eagles along the shore. The nearby Eastern Miombo woodlands are home to African wild dogs. Swimming, snorkelling and diving are popular activities in the tropical waters of the lake, and many visitors also enjoy waterskiing, sailing and fishing. There are many options available for holiday accommodation at the lake, including resorts, guesthouses and caravan or camping parks. All budgets are catered for, with luxury lodges attracting the glamorous and humble campsites hosting families and backpackers. Cape Maclear is a well-developed lakeside town, and nearby Monkey Bay is a great holiday resort area. Club Makokola, near Mangochi, is also a popular resort. -
The Identity of Pseudotropheus Elongatus, with the Description of P. Longior from Mbamba Bay, Tanzania, and Notes on Genyochromis Mento (Teleostei: Cichlidae)
97 Ichthyol. Explor. Freshwaters, Vol. 7, No.2, pp. 97-110,12 figs.,1 tab., September 1996 © 1996 by Verlag Dr. Friedrich Pfeil, Miinchen, FRG- ISSN 0936-9902 The identity of Pseudotropheus elongatus, with the description of P. longior from Mbamba Bay, Tanzania, and notes on Genyochromis mento (Teleostei: Cichlidae) Lothar Seegers * Although Pseudotropheus elongatus was originally described from Mbamba Bay, Tanzania, a species of the P. elongatus-complex from Nkhata Bay, Malawi, has been considered to be the typical P. elongatus. Collections from Mbamba Bay revealed that at least two elongate Pseudotropheus species co-occur. The two extant syntypes of P. elongatus belong to the two species from Mbamba Bay. The specimen pictured by Fryer (1956) is selected as lectotype. The other species is described here as P. longior, new species. A third elongate cichlid, frequent at Mbamba Bay, is Genyochromis menta; some observations on this fish are included. 1956 beschrieb Fryer Pseudotropheus elongatus von Mbamba Bay, Tanzania, wahrend in der Literatur bisher eine Form aus dem P. elongatus-Komplex von Nkhata Bay, Malawi, als P. elongatus im Sinne der Typen angesehen wurde. In Mbamba Bay gibt es zwei gestreckte Pseudotropheus-Arten. Die beiden existierenden Syntypen gehoren unterschiedlichen Taxa an, namlich jeweils einer der beiden bei Mbamba Bay vorkommenden gestreckten Pseudotropheus-Arten. Als Lectotypus fur P. elongatus wurde das Exemplar festgelegt, das von Fryer (1956) abgebildet wurde. Die andere Pseudotropheus-Art wird hier als Pseudotropheus longior n. sp. beschrieben. Eine dritte gestreckte Cichlidenart, die in Mbamba Bay haufig vorkommt, ist Genyochromis menta Trewavas, 1935. Zu dieser Art werden einige Beobachtungen mitgeteilt. -
Mayan Cichlid (Cichlasoma Urophthalmum) Ecological Risk Screening Summary
U.S. Fish and Wildlife Service Mayan Cichlid (Cichlasoma urophthalmum) Ecological Risk Screening Summary Web Version – 11/01/2012 Photo: Alexander Calder 1 Native Range, and Status in the United States Native Range From Robins (2001): The Mayan cichlid is native to the Central American Atlantic slope waters of southeastern Mexico (including the Yucatán Peninsula), Belize, Guatemala, Honduras, and Nicaragua. Nonindigenous Occurrences From Schofield et al. (2011): “This species was first documented in Florida when specimens were observed and collected and observed in Everglades National Park in 1983; it is established in several areas in and around the park (Loftus 1987; Lorenz et al. 1997; Smith-Vaniz, personal communication [not cited]; Tilmant 1999) and Big Cypress National Preserve (Nico, unpublished data; Tilmant 1999).” “On the east side of Florida it has been recorded from Canal C-111 north to the Little River Canal (C-7 Canal) (Shafland 1995).” Cichlasoma urophthalmus Ecological Risk Screening Summary U.S. Fish and Wildlife Service – Web Version – 11/1/2012 “A single specimen was taken from a rock pit in Manatee County in October 1975 (Smith- Vaniz, personal communication [not cited]).” “Mayan ciclids have also been collected in Lake Okeechobee and Lake Osbourne, Palm Beach County in 2003 (Cocking 2003; Werner 2003).” “A new population was found in Charlotte Harbor in the summer of 2003 (Adams and Wolfe 2007; Associated Press 2003; Charlotte Harbor NEP 2004; Byrley, personal communication [not cited]). This is the most northern population known.” Reported established in Florida Panther National Wildlife Refuge (2005).” “A specimen was collected in Holiday Park in Broward County (International Game Fishing Association 2000).” “In 2006, this species was found to be established in Mobbly Bayou in Tampa Bay and in canals on Merritt Island in 2007 (Paperno et al. -
Blackchin Tilapia (Sarotherodon Melanotheron) Ecological Risk Screening Summary
U.S. Fish and Wildlife Service Blackchin Tilapia (Sarotherodon melanotheron) Ecological Risk Screening Summary Web Version – 10/01/2012 Photo: © U.S. Geological Survey From Nico and Neilson (2014). 1 Native Range and Nonindigenous Occurrences Native Range From Nico and Neilson (2014): “Tropical Africa. Brackish estuaries and lagoons from Senegal to Zaire (Trewavas 1983).” Nonindigenous Occurrences From Nico and Neilson (2014): “Established in Florida and Hawaii. Evidence indicates it is spreading rapidly in both fresh and salt water around island of Oahu, Hawaii (Devick 1991b).” “The first documented occurrence of this species in Florida was a specimen gillnetted by commercial fishermen in Hillsborough Bay near Tampa, Hillsborough County, in 1959 (Springer and Finucane 1963). Additional records for the western part of the state indicate that this species is established in brackish and freshwaters in eastern Tampa Bay and in adjoining drainages in Hillsborough County, ranging from the Alafia River south to Cockroach Bay. The species has been recorded from the Alafia River from its mouth up to Lithia Springs; from the Hillsborough River, Bullfrog Creek, the Palm River, and the Little Manatee River; and from various western drainage and irrigation ditches (Springer and Finucane 1963; Finucane and Rinckey 1967; Buntz Sarotherodon melanotheron Ecological Risk Screening Summary U.S. Fish and Wildlife Service – Web Version – 10/01/2012 and Manooch 1969; Lachner et al. 1970; Courtenay et al. 1974; Courtenay and Hensley 1979; Courtenay and Kohler 1986; Lee et al. 1980 et seq.; Courtenay and Stauffer 1990; DNR collections; UF museum specimens). There are two records of this species from the west side of Tampa Bay, in Pinellas County: a collection from Lake Maggiore in St. -
Sustainable Development Impacts of Investment Incentives
Sustainable Development Impacts of Investment Incentives A Case Study of Malawi’s Tourism Sector Nelson Nsiku and Sheila Kiratu 2009 trade knowledge network Abstract This study seeks to determine the link between investment incentives and foreign direct investment (FDI) flows in Malawi’s tourism sector and also to question whether these incentives have promoted sustainable development in the country. It finds that investment incentives do not determine FDI in the tourism sector; rather, decisions to invest were largely driven by the the country’s natural resources; the cost of raw materials; the availability of relatively cheap labour; and the inflation, foreign exchange and interest rates. This suggests that the type, nature and quantity of FDI in the tourism sector is shaped by other government policy such as promoting increased private sector participation rather than by investment incentives per se. It therefore follows that this has implications for Malawi’s sustainable development goals, especially the role of investment incentives in shaping the economic and social impacts of investment, as well as environmental impacts, which the incentives seem to have affected negatively. About the authors Nelson Nsiku is a lecturer in Economics at the University of Malawi Polytechnic and is a member of several national associations and committees that contribute to the policy debate on economic planning and trade policy in Malawi. Sheila Kiratu is an advocate of the High Court of Kenya and a trade and investment lawyer with research interests in sustainable development, climate change, energy and investment. She is currently the coordinator of the Trade Knowledge Network Southern Africa branch. -
SOCIAL ISOLATION and AGGRESSIVENESS in the AMAZONIAN JUVENILE FISH Astronotus Ocellatus
SOCIAL ISOLATION AND AGGRESSIVENESS IN THE AMAZONIAN JUVENILE FISH Astronotus ocellatus GONÇalves-DE-Freitas, E.1 and MARIGUELA, T. C.2 1Laboratório de Comportamento Animal, Departamento de Zoologia e Botânica, IBILCE/UNESP, (CAUNESP, RECAW), R. Cristóvão Colombo, 2265, CEP 15054-000, São José do Rio Preto, SP, Brazil 2Programa de Pós-Graduação em Zoologia, IB, UNESP, Distrito de Rubião Jr, CEP 18618-000, Botucatu, SP, Brazil Correspondence to: Eliane Gonçalves-de-Freitas, Laboratório de Comportamento Animal, Departamento de Zoologia e Botânica, IBILCE/UNESP, (CAUNESP, RECAW), R. Cristóvão Colombo, 2265, CEP 15054-000, São José do Rio Preto, SP, Brazil, e-mail: [email protected] Received July 15, 2003 – Accepted March 23, 2004 – Distributed February 28, 2006 (With 2 figures) ABSTRACT We tested the effect of social isolation on the aggressiveness of an Amazonian fish: Astronotus ocellatus. Ten juvenile fishes were transferred from a group aquarium (60 x 60 x 40 cm) containing 15 individuals (without distinguishing sex) to an isolation aquarium (50 x 40 x 40 cm). Aggressiveness was tested by means of attacks on and displays toward the mirror image. The behavior was video-recorded for 10 min at a time on 4 occasions: at 30 min, 1 day, 5 days and 15 days after isolation. The aggressive drive was analyzed in three ways: latency to display agonistic behavior, frequency of attacks and specific attacks toward the mirror image. The latency to attack decreased during isolation, but the frequency of mouth fighting (a high aggressive attack) tended to increase, indicating an augmented aggressive drive. Our findings are congruent with the behavior of the juvenile cichlid, Haplochromis burtoni but differ from the behavior observed in another cichlid, Pterophylum scalare. -
Ecology of the Mayan Cichlid, Cichlasoma Urophthalmus Günther, in the Alvarado Lagoonal System, Veracruz, Mexico
Gulf and Caribbean Research Volume 17 Issue 1 January 2005 Ecology of the Mayan Cichlid, Cichlasoma urophthalmus Günther, in the Alvarado Lagoonal System, Veracruz, Mexico Rafael Chavez-Lopez Universidad Nacional Autonoma de Mexico Mark S. Peterson University of Southern Mississippi, [email protected] Nancy J. Brown-Peterson University of Southern Mississippi, [email protected] Ana Adalia Morales-Gomez Universidad Nacional Autonoma de Mexico See next page for additional authors Follow this and additional works at: https://aquila.usm.edu/gcr Part of the Marine Biology Commons Recommended Citation Chavez-Lopez, R., M. S. Peterson, N. J. Brown-Peterson, A. Morales-Gomez and J. Franco-Lopez. 2005. Ecology of the Mayan Cichlid, Cichlasoma urophthalmus Günther, in the Alvarado Lagoonal System, Veracruz, Mexico. Gulf and Caribbean Research 17 (1): 123-131. Retrieved from https://aquila.usm.edu/gcr/vol17/iss1/13 DOI: https://doi.org/10.18785/gcr.1701.13 This Article is brought to you for free and open access by The Aquila Digital Community. It has been accepted for inclusion in Gulf and Caribbean Research by an authorized editor of The Aquila Digital Community. For more information, please contact [email protected]. Ecology of the Mayan Cichlid, Cichlasoma urophthalmus Günther, in the Alvarado Lagoonal System, Veracruz, Mexico Authors Rafael Chavez-Lopez, Universidad Nacional Autonoma de Mexico; Mark S. Peterson, University of Southern Mississippi; Nancy J. Brown-Peterson, University of Southern Mississippi; Ana Adalia Morales- Gomez, Universidad Nacional Autonoma de Mexico; and Jonathan Franco-Lopez, Universidad Nacional Autonoma de Mexico This article is available in Gulf and Caribbean Research: https://aquila.usm.edu/gcr/vol17/iss1/13 Book for Press.qxp 2/28/05 3:30 PM Page 123 Gulf and Caribbean Research Vol 17, 123–131, 2005 Manuscript received July 18, 2004; accepted September 20, 2004 ECOLOGY OF THE MAYAN CICHLID, CICHLASOMA UROPHTHALMUS GÜNTHER, IN THE ALVARADO LAGOONAL SYSTEM, VERACRUZ, MEXICO Rafael Chávez-López, Mark S. -
Rare Morph Lake Malawi Mbuna Cichlids Benefit from Reduced Aggression from Con- and Hetero-Specifics
bioRxiv preprint doi: https://doi.org/10.1101/2021.04.08.439056; this version posted April 9, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC 4.0 International license. 1 Rare morph Lake Malawi mbuna cichlids benefit from reduced aggression from con- and hetero-specifics 2 Running title: Reduced aggression benefits rare morph mbuna 3 4 Alexandra M. Tyers*, Gavan M. Cooke & George F. Turner 5 School of Biological Sciences, Bangor University, Deniol Road, Bangor. Gwynedd. Wales. UK. LL57 2UW 6 * Current address: Max Planck Institute for Biology of Ageing, Joseph-Stelzmann-Straße 9B, 50931, Köln 7 8 Corresponding author: A.M. Tyers, [email protected] 9 10 Abstract 11 Balancing selection is important for the maintenance of polymorphism as it can prevent either fixation of one 12 morph through directional selection or genetic drift, or speciation by disruptive selection. Polychromatism can 13 be maintained if the fitness of alternative morphs depends on the relative frequency in a population. In 14 aggressive species, negative frequency-dependent antagonism can prevent an increase in the frequency of rare 15 morphs as they would only benefit from increased fitness while they are rare. Heterospecific aggression is 16 common in nature and has the potential to contribute to rare morph advantage. Here we carry out field 17 observations and laboratory aggression experiments with mbuna cichlids from Lake Malawi, to investigate the 18 role of con- and heterospecific aggression in the maintenance of polychromatism and identify benefits to rare 19 mores which are likely to result from reduced aggression. -
Kenyi Cichlid (Maylandia Lombardoi) Ecological Risk Screening Summary
Kenyi Cichlid (Maylandia lombardoi) Ecological Risk Screening Summary U.S. Fish and Wildlife Service, April 2011 Revised, July 2018 Web Version, 8/3/2018 Photo: Ged~commonswiki. Public domain. Available: https://commons.wikimedia.org/wiki/File:Maylandia_lombardoi.jpg. (July 2018). 1 Native Range and Status in the United States Native Range From Kasembe (2017): “Endemic to Lake Malawi. Occurs at Mbenji Island and Nkhomo reef [Malawi].” From Froese and Pauly (2018): “Africa: Endemic to Mbenji Island, Lake Malawi [Malawi].” 1 Status in the United States This species has not been reported as introduced or established in the United States. This species is in trade in the United States. From Imperial Tropicals (2018): “Kenyi Cichlid (Pseudotropheus lombardoi) […] $ 7.99 […] UNSEXED 1” FISH” Means of Introductions in the United States This species has not been reported as introduced or established in the United States. Remarks There is taxonomic uncertainty concerning Maylandia lombardoi. Because it has recently been grouped in the genera Metriaclima and Pseudotropheus, these names were also used when searching for information in preparation of this assessment. From Kasembe (2017): “This species previously appeared on the IUCN Red List in the genus Maylandia but is now considered valid in the genus Metriaclima (Konings 2016, Stauffer et al. 2016).” From Seriously Fish (2018): “There is ongoing debate as to the true genus of this species, it having been variously grouped in both Maylandia and Metriaclima, as well as the currently valid Pseudotropheus.