Children’s Ministry

Our Sunday School Program is active and vibrant as children of all ages learn about God.

Noah’s Ark Nursery (0 to 30 months)

contact: Mary Okada                                                    Return to Home Page

In this safe and clean environment, infants and toddlers are lovingly cared for by trained caregivers where they learn about God’s love through music, activities, and story telling.

Lighthouse Ministry (30 months to 5th grade)

contact: Brenda Lu

Every Sunday, children are taught God’s word in a fun, creative environment.  Children learn about God through Bible stories, songs, crafts and fun activities.  In the summer, Vacation Bible School provides children with a daily program aimed at teaching children about God in a group environment.  The children also star in our special Children’s programs for Easter and Christmas.

Purpose

To love and nurture our children so that they can experience the love of God, come to know Him as their Lord and Savior, and to grow to maturity in Christ.

Values

  • Child-Targeted; fun and safe child oriented environment.
  • Biblical teaching which is relevant and creative.  Instills desire for life long learning.
  • Mentoring and caring for adults and children in small groups where we can model an authentic relationship with Jesus Christ.
  • Reaching out and bringing in unchurched children.
  • Oneness in Christ expressed in the diversity of all people.

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Eurasian Curlew Numeniusarquata

widespread species remains common in many parts of its range, and determining population trends is problematic. Nevertheless, declines have been recorded wholesale jerseys in several key populations and

overall a moderately rapid global decline is estimated. 2003. AERC TAC Checklist of bird taxa occurring in Western Palearctic region, 15th Draft. Cramp, S.; Perrins, C. M. 1977 1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.55cm. Large wader with long down curved bill. Mottled or streaked brown plumage with whiter belly and undertail. In flight show pointed whitish rump and barred tail as well as mottled whitish underwings. Outer primaries contrastingly dark and flight slow and gull like. Similar spp. It winters around the coasts of north west Europe, the Mediterranean, Africa, the Middle East, the Indian Subcontinent, South East Asia, Japan and the Sundas. It has a large global population estimated to number 765,000 1,065,000 individuals (M. Barter in litt. 2007; Wetlands International 2006). The breeding population in Western Europe (220,000 360,000 pairs) has declined in recent years, with a 53% decline in the United Kingdom calculated over the period 1970 2005 from the Common Birds Census and the Breeding Bird Survey, and a 37% decline over the period 1994 2006 derived from the Breeding Bird Survey (Eaton et al. 2007; R. Gregory in litt. 2007). A decline of 86% was calculated in Ireland between 1988 1991 and 2003 (Gibbons et al. 1993; Hillis 2003) and declines have been recorded in Finland (BirdLife International 2004), Germany (Htker et al. 2007), Lithuania (20 30% per decade) (L. Raudonikis in litt. 2007) and the Netherlands (31% since 1984 (A. J. van Djik in litt. 2007)). Unquantified, but potentially highly significant, declines have also been recorded in the central Asian cheap wholesale jerseys populations of N. a. orientalis (J. Kamp and S. Sklyarenko in litt. 2007). In Denmark (K. N. Flensted in litt. 2007; Meltofte et al. 2009) and eastern Siberia (I. wholesale nba jerseys china Fefelov in litt. 2007) breeding populations are apparently stable and apparent increases in wintering populations in the Wadden Sea (Laursen and Karsten 2005; Meltofte et al. 2009), on the Adriatic coast (Gusson et al. 2005), in East Asia (M. Barter in litt. 2007) and in Western Europe suggest that breeding populations, probably in European Russia and northern Siberia have perhaps increased. Overall, analysis of the compiled trend data indicate three generation (15 year) estimate of decline of between 26% and 34% (BirdLife International 2004; Hillis 2003; A. J. van Djik in litt. 2007; M. Barter in litt. 2007; Wetlands International 2006; Thorup 2006; A. Copland in litt. 2007; M. Boschert in litt. 2007; Eaton et al. 2007; R. Gregory in litt. 2007). Owing to the uncertainty over whether declines in southern populations have been compensated by increases in northern populations, the global trend is suspected to fall within the band 20 30% declines in the past 15 years or three generations.

c.1,000 10,000 individuals on migration and c.50 1,000 wintering individuals in Taiwan; c.1,000 10,000 individuals on migration and c.1,000 10,000 wintering individuals in Korea;

c.1,000 10,000 individuals on migration and c.50 1,000 wintering individuals in Japan and c.10,000 100,000 breeding pairs and c.1,000 10,000 individuals on migration in Russia (Brazil

Data from 2007 return estimated three generation declines of 26.1 34.1%. 1996) and breed from April to August (Hayman et al. 1986) in solitary territorial pairs (Johnsgard 1981), occasionally also forming small colonies (Flint et al. 1984). After breeding adults gather on coasts (from July onwards) (Hayman et al. 1986) for the post breeding moult (Snow and Perrins 1998) before migrating south to the wintering grounds between July and November (del Hoyo et al. 1996). The species departs its wintering grounds again from February through to May, although non breeders may remain in the wintering areas all year round (del Hoyo et al. 1996). During the winter the species usually forages singly or in small groups (del Hoyo et al. 1996) occasionally aggregating into flocks of several thousand individuals, especially at roosting sites (Snow and Perrins 1998). Habitat Breeding The species breeds on upland moors, peat bogs, swampy and dry heathlands, fens, open grassy or boggy areas in forests, damp grasslands, meadows (del Hoyo et al. 1996), non intensive farmland in river valleys (Hayman et al. 1986), dune valleys and coastal marshlands (del Hoyo et al. 1996) Non breeding During the winter the species frequents muddy coasts, bays and estuaries (del Hoyo et al. 1996) with tidal mudflats and sandflats (Snow and Perrins 1998), rocky and sandy beaches with many pools (Johnsgard 1981; Snow and Perrins 1998), mangroves, saltmarshes (Snow and Perrins 1998), coastal meadows (Johnsgard 1981) and muddy shores of coastal lagoons (Johnsgard 1981), inland lakes and rivers (del Hoyo et al. 1996). It also utilises wet grassland and arable fields during migration (del Hoyo et al. 1996). Diet Its diet consists chiefly of annelid worms and terrestrial insects (del Hoyo et al. Coleoptera and Orthoptera) (Johnsgard 1981) especially during the summer (del Hoyo et al. 1996), although it will also take crustaceans, molluscs, polychaete worms (del Hoyo et al. 1996), spiders (Johnsgard 1981), berries and seeds, as well as occasionally small fish, amphibians, lizards, young birds and small rodents (del Hoyo et al. 1996). Breeding site The nest is a shallow depression on the ground or on a mound (Flint et al. 1984) in the open or in the cover of grass or sedge (del Hoyo et al. 1996) often far from water (Johnsgard 1981). 1996; Johnsgard 1981) and of marginal grassland habitats as a result of agricultural intensification and improvement (del Hoyo et al. drainage, inorganic fertilisation and reseeding) (Baines 1988). The species also suffers from high egg and chick mortalities (due to mechanical mowing) and higher predation rates if nesting on improved grasslands (del Hoyo et al. 1996). Conversely populations in the central Asians steppes have declined following abandonment of farmland and subsequent increases in the height of vegetation, rendering large areas unsuitable for nesting. It has also suffered population declines as a result of hunting (Johnsgard 1981), and is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Non breeding Wintering populations are threatened by disturbance on intertidal mudflats (del Hoyo et al. 1996; Burton et al. from construction work (Burton et al. 2002a) and foot traffic (Burton et al. 2002b)), development on high tide roosting sites, pollution (del Hoyo et al. 1996) and the flooding of estuarine mudflats and saltmarshes as a result of tidal barrage construction (Burton 2006). The species is also threatened by the degradation of migrational staging areas owing to land reclamation, pollution, human disturbance and reduced river flows (Kelin and Qiang 2006). Local populations of this species have also declined owing to hunting pressures (del Hoyo et al. 1996).

Conservation Actions UnderwayAnnex II/2 of the EU Birds Directive. A management plan for the species, updated for 2007 2009, was published in 2007, covering the EU portion of the species’s range (Jensen and Lutz 2007). A 5 year moratorium on hunting the species was implemented in France in July 2008 (A. Duncan in litt. 2008). The species occurs in cheap nfl jerseys a large number of protected areas throughout its range and features in several national monitoring schemes. Conservation Actions ProposedThe Management Plan for Curlew outlines key conservation targets: Protect key wintering sites. Determine the key parameters driving declines in breeding areas and integrate agri environment measures to counter these. Continue monitoring trends. 1988. The effects of improvement of upland grassland on the distribution and density of breeding wading birds (Charadriiformes) in northern England. Biological Conservation 45: 221 236.

BirdLife International. 2004. Birds in Europe: population estimates, trends and conservation status.

Brazil, M. 2009. Birds of East Asia: eastern China, Taiwan, Korea, Japan, eastern Russia. Christopher Helm, London.

Burton, N. H. K. 2006. The impact of the Cardiff Bay barrage on wintering waterbirds. In: Boere, G.; Galbraith, C., Stroud, D. (ed.), aterbirds around the world, pp. 805. The Stationary Office, Edinburgh, UK.

Burton, N. H. K.; Armitage, M. J. S.; Musgrove, A. J.; Rehfisch, M. M. 2002. Impacts of Man Made landscape Features on Numbers of Estuarine Waterbirds at Low Tide. Environmental Management 30(6): 857 864.

Burton, N. H. K.; Rehfisch, M. M.; Clark, N. A. 2002. Impacts of Disturbance from Construction Work on the Densities and Feeding Behavior of Waterbirds using the Intertidal Mudflats of Cardiff Bay, UK. Environmental Management 30(6): 865 871.Articles Connexes:superintendent sentenced for fraud San Diego The former superintendent of elementary schools in El Centro was sentenced to 10 months in federal cheap michael kors custody Monday for submitting false results on standardized school science tests and bogus reimbursement claims.Dr. Michael Klentschy, 68, built a national reputation beginning in the 1980s as an innovator in how to teach science to elementary school children. His “kit based” methodology won numerous converts and awards as well as a steady flow of research grants and work for Klentschy as a consultant.But in pleading guilty in San Diego federal court to wire fraud charges, Klentschy who headed the El Centro district from 1994 to his abrupt retirement in 2007 acknowledged test scores from district students for the 2004 05 Michael Kors outlet school year that he submitted as part of a federal grant were false and discount michael kors inaccurate. Attorney’s Office said that 75 percent of the test scores that Klentschy submitted in 2004 05 had been falsified, according to Michael Kors outlet court records.The scores were part

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