Laguna San Ignacio: profile

GENERAL   SOURCE
Site Laguna San Ignacio, Baja California Sur, México.  
Map Landsat TM images (scale 1:50,000)  
Location It is located at 26º43’-26º58’ N and 113º08 - 113º16 W, on the Pacific coast of the state of Baja California Sur 1
Contact Proesteros (61) 78 01 62 or (61) 78 60 50.

Biosphere Reserve El Vizcaino (115) 7 17 77

Centro de Investigaciones Biologicas del Noroeste (CIBNOR) Tel (1) 125-36-33 FAX (1) 125 47 15

 
Approximate wetland habitat area About 17,500 ha. 1,2
Approximate historic area About 17,500 ha  
OWNERSHIP OWNER APPROX. AREA SOURCE
LAGUNA SAN IGNACIO Ejido Emiliano Zapata 112,500 ha 4, 8
  Ejido San Ignacio 107,226 ha 4, 8
  Propiedad privada    
  Terrenos nacionales y asignacion especial    
  Fundo minero    
LAND USE   SOURCE
Land use designation International attempts to protect the site include, the Migratory Bird Treaty that was signed by Mexico and the United States of America on 9 January 1937, in order to protect migratory birds and game mammals. In 1949 Mexico adheres to the International Whale Commission to protect and enforce the rational use of whale resources.

By federal decree, on 11 September 1972, Lagunas San Ignacio and Ojo de Liebre were designated as "Zones of Reserve and refuge of Migratory Birds and other Wildlife".

Another decree, on 16 July 1979 designated this lagoon as "Refuge for Gravid Whales and Cubs and Zone of Maritime touring attraction". Laguna San Ignacio is part of the Biosphere Reserve El Vizcaino (2,546,790.25 ha), decree on 30 November 1988.

5, 6, 7, 8
Onsite use Prime gray whale-watching destination, artisanal (small-scale) fishery, oyster-aquaculture, seasonal clam and blue crab fishery, recreational, bird-watching tourism, open space, research and teaching activities. 33, 36
Historic use Cochimí nation used the area for hunting, fishing and gathering of mollusk, fish, sea turtles and marine mammals. Fisheries 9
Adjacent use Several fishermen camps, most of them are permanent, others and a rustic hotel are used only during the winter whale-watching season. The most important communities are La Bocana, Punta Abreojos, La Laguna, La Base, La Freidera, and El Cardon.

Scattered cattle ranches along the tributaries of the watershed

 
Historic adjacent use Cattle ranching along the main arroyos that empty into the lagoon. In 1855 indiscriminated hunting over whale, elephant seal, sea lion and sea otter hunting. In 1940 the first fishermen communities were settled between Laguna San Ignacio and Punta Eugenia. 4, 10
HYDROLOGY   SOURCE
Tidal influence Tides on the west coast of the Baja California peninsula are semidiurnal (two periods of flow and two of ebb-tides in a daily cycle). On Isla de Cedros, the closest tidal station, maximun tidal range is 3.1 m and the average is 1.6 m. 3
Wetland watershed area The San Miguel - Arroyo del Vigía is about 14,591 km2 in the state of Baja California Sur. Laguna San Ignacio is located in hydrological region 2 (Baja California Centro -Oeste "Vizcaino" )and encompasses two watersheds: Laguna San Ignacio-Arroyo San Raymundo (11,187 km2 ) and San Miguel-Arroyo el Vigia (14,591 km2). However, four subwatersheds surround the lagoon: Arroyo del Vigia, Laguna de San Ignacio (9,150 km2), Río San Ignacio and Arroyo San Patrocinio. 2, 3
TRIBUTARIES AND FLOW TRIBUTARY FLOW SOURCE
Arroyos have a well defined bed, but they are intermittent. Sometimes, they do discharge into the Pacific Ocean through the

Laguna San Ignacio, but very often they dry (because of infiltration) before they reaching the shoreline. The only permanent arroyo in the area is arroyo San Ignacio, but with no influence on the surrounding area.

Main arroyos draining the area and emptying into Laguna San Ignacio are: arroyo El Granado (25 km long, with a drainage area of 384,000 m2 and a mean annual volume of 914.4 m3 ); arroyo La Higuera (32 km long, draining an area of 275000 m2 and an annual volume of 1276.8 m3); arroyo Palo Verde (37 km long, an area of 275000 m2 and a annual volume of 1722.4m3); arroyo Salvioso (29 km long, an area of 319,000 m2 and a volume of 1060.7 m3), arroyo San Ignacio (37 km long, an area of 444,000 m2 and a volume of 1476.3 m3); arroyo Patrocinio (39 km long, an area of 429,000 m2 and a volume of 1426.4 m3); other arroyos that empty into the lagoon are: Batequi, San Angel, Covarrubias, San Juan, San Hilario y Santa Rosa. These arroyo run only during the rainy season. However most of the water is lost, due to lack of infrastructure for water retention. In average, tributary subwatersheds have a runoff coeficiente of 5%. 3
Dams None    
Other source Average annual runoff is 0-20 mm, hence annual global infiltration and aquifer recharge is null or very low. Therefore, aquifers are considered as fragile and in danger of overexploitation. In the region called North Pacific there is no underground water and water supplies come from desalting plants and from Valle de Vizcaíno through the aqueduct Vizcaíno-Pacífico Norte.

The aquifers recharged by the subwatersheds laguna San Ignacio and Rio San Ignacio are in equilibrium or with some available water. San Ignacio subwatershed, has 3.5 millions m3 available, based on estimeates that recharge is 8.5, whereas extraction is 5.0 millions m3

  11
WATER QUALITY   SOURCE
General In a 1994 study, quality of exploitated underground water resulted to be from moderate to bad quality. Some samples were up to 3900 ppm of total dissolved solids, and the predominant type of water was sodic-clorinated. A study in 1978, assessed coliform bacteria in Laguna San Ignacio and Estero el Cardón. Ninety-four percent of the samples contained less than 1.8 or 2.0 total coliforms/100ml for both lagoons. Such levels are very low, according to Mexican and other countries legislation. Therefore, quality in this regard is very good and compsumption of any product from this lagoon do not represent any risk to public health. However, another analysis (fecal and total coliforms) in 1994 for the interior part of Laguna San Ignacio showed a bacteria concentration of 13NMP/100 ml, this value is considered high, relative to the small amount of human settlements on the margins of the lagoon, but still is below the maximun concentration alloed by environmental regulation (200 NMP/100 ml for coastal areas and 14 NMP/100ml and up to 43 NMP/100ml for aquaculture). 3, 12
Dissolved oxygen (DO) Mean values for Laguna San Ignacio are 5.37-5.74 ml/lt, but ranges go from 3.48 to 9.9 ml/lt. No differences were noticed during low and high tide.

At Estero El Cardón, mean values were 5.22-5.46 ml/lt. Range was from 3.58 to 9.9 ml/lt..

12
Water salinity Water salinity increases from the mouth (36 ppt) to the head (41 ppt). No significant differences were observed between bottom and surface. 3
Sedimentation Sedimentation levels were less than 0.1 ml/lt, probably because sediments are large coarse (sand) which sink relatively fast. However, it is evident that there is a large movement of materials during tidal fluxes, since a large extension of shore is affected. Sediments are mostly composed by sand and in some parts by mud. 3
SOIL   SOURCE
  Soil surrounding the lagoon is mostly Solonchak. This soil type is (< 40% of saturation of interchangeable sodium). Other types of soils around the lagoon include a mixture of Solonchak ortico, Regosol eutrico and Regosol calcarico. These are characterized by a coarse texture and strongly sodic. 3, 8
HABITAT AREA VEGETATION SOURCE
Tidal channel/Mudflat

There is a channel

6 m deep and 680 m wide, that crosses the banks to access the lagoon. About 4 km north of Punta Bronaugh, where the lagoons widens, the channel also enlarges to an area of 2 km2 and between 9 and 14 m deep. Starting from this zone, there are three channels, the principal one is 3.75 km long and in average 6 m deep, it goes toward the head of the lagoon. The head of the lagoon has extensive areas subject to flooding.

  A total of 127 species of algae has been reported for Laguna San Ignacio by different studies.

Thirteen species of algae, were reported for Laguna San Ignacio between 1953 and 1961, but no specific location or date of collection was mentioned.

In a 1994 study, 30 species of algae are listed, some of them with commercial value such as Gelidium spp and Euchemia spp.

A 1995 study listed 31 species of algae for the west coast of the El Vizcaino Biosphere Reserve distributed between open littoral and inner littoral.

An 1992-1993 study on the phycological flora of the lagoon, reported

85 species. Of these, 48 were Rhodophyceae (56.5%), 21 Chlorophyceae (24.7%), 14 Phaeophyceae (16.5%) and two Cyanophyceae (2.3%). Seventy-six species were first records for the site. Laguna San Ignacio hosts extensive areas of sea grass Zostera marina, principal food for the Black Brant (Branta bernicla). Other species from the submerged zones include: Ruppia maritima and Phyllospadix scouleri.

A 1983 study on the phytoplancton of Estero El Cardon, reported 139 species, out of which 55 were centric diatoms, 65 penned diatoms and 19 flagellades. Phytoplancton showed in patches with higher densities in the interior part of the estero during November and December.

4, 11, 13, 14, 15, 16, 17, 18, 19, 20, 21
Saltmarsh

Toward the interior of the lagoon there exist extensive areas of saltmarsh. This vegetation is mostly represented by: Batis maritima, Salicornia bigelovii, Spartina foliosa and Monanthochloe littoralis.

  A total of species of plants have been reported by different studies, for all habitats in Laguna San Ignacio, have a special status designation and are non-native species. A 1991 study listed 447 species of vascular plants for the whole El Vizcaino Biosphere Reserve, out of which ---- can be found in the environs of the lagoon. In a 1994 study, 85 species of plants were recorded in four types of vegetation. The most abundant species of hallophytic vegetation were: Salicornia subterminalis (93.75%) and Frankenia palmeri ( 6.25%), other associated species were: Salicornia pacifica, Atriplex spp., Allenrolfea sp., Suaeda sp. y Limonium sp. 2, 4, 8
Transition (Mangroves, Dunes, coastal vegetation)

Considerable extensions of mangrove are found at the entrance to the mouth of the lagoon, and at the Esteros El Cardon, La Pitahaya and El Delgadito, south of the mouth of the lagoon.

  A 1974 review of pacific coast beach vegetation of North America reported 46 characteristic beach species, out of which, 10 can be found between latitude 28° and 27°.

In a 1972-1975 sample of dune vegetation Abronia maritima was found along the entire coast. This species is the major foredune builder and it is joined at the central sector of the peninsula by Sesuvium portulacastrum.

A 1994 study showed that the most dominant mangrove species were: Laguncularia racemosa in flooded areas and Rhizopohora mangle in permanent inundated zones. Other species associated to this type of vegetation are Salicornia virginica, Salicornia subterminalis, Batis maritima, Monanthochloe littoralis, Atriplex sp, Suaeda mexicana, Mesembryanthemum crystallinum, Abronia maritima and Distichlis spicata.

Coastal dune vegetation varies, but the most commonly found species are: Abronia maritima, Abronia gracilis, Ambrosia dumosa, Atriplex barclayana, Atriplex canescens, Dalea maritima, Mesembryanthemum crystallinum, Salicornia spp. and Distichlis spicata.

 

2, 4, 8, 22, 23
Uplands   A 1994 study, classified upland vegetation around the lagoon in four types (matorral sarcocaule, matorral micrófilo, matorral halófilo and hallophuytic vegetation), each one constituted by diverse associations. At the matorral sarcocaule the Yucca valida-Pachycereus pringlei association is dominated by: Opuntia cholla (25.54%), Encelia palmeri (24.09%), Jatropha vernicosa (18.25%), Ambrosia dumosa (8.03%) and Larrea tridentata (6.57%). The matorral micrófilo include three associations: in the Fouquieria-Frankenia association, the most abundant species are: Frankenia palmeri (80.30%), Ambrosia dumosa (10.61%) and Haplopappus spinulosus (4.55%). In the Lycium-Ambrosia association, the most abundant species are: Ambrosia dumosa ( 46.67%), Lycium spp. (43.33%) and Larrea tridentata (6.67%); and last, in the Lycium-Atriplex association, the dominant species are: Salsola kali (44.19%), Atriplex barclayana (12.79%) and Spharalcea ambigua (12.79%).

The hallophytic matorral is the least diverse and it is represented by the Atriplex spp. association, the most abundant species are: Atriplex barclayana (58%), Atriplex canescens (29.41%), and Encelia sp. (11.76%).

4
ANIMAL USE   SOURCE
Birds A total of 221 species of birds have been documented for the site, out of which 47 are sensitive species and 3 are non-native species.

A total of 20 species of ducks and one specie of brant winters in Laguna San Ignacio.The average numbers of ducks anually recorded between 1977-1978 were 5,289. Between 1954 and 1989, the average number of wintering brant (Branta bernicla nigricans) in this site was 33,278. During a 1988 and 1989 study, a total of 54 species of birds were recorded at San Ignacio Lagoon, 44 were observed at ballena island. Nine waterbird species breed on this island. A 1991-1992 survey of Snowy plover (Charadrius alexandrinus) reported a total of 1344 adults in 16 localities, of these, 378 (28% ) were found in the Laguna San Ignacio complex.

A 1991-1994 survey estimated 354,900 wintering shorebirds in wetlands on the west coast of Baja California. Of these, 8.9 % were located in the Laguna San Ignacio complex. A total of 31,542 wintering shorebirds were estimated in January 1993, with large species making up 27.7%, medium 10.3.0% and small 62.1% of the total.

San Ignacio complex is a major wintering site for Brant (>33,000) and Shorebirds (32,000).

A 1994 study, listed a total of 173 species of birds. Within seabirds the most abundant are Gaviformes, such as Gavia pacifica and Gavia immer; and

Pelecaniformes, such as Pelecanus occidentalis and Phallacrocorax auritus; and Anseriformes, principally the Black Brant Branta bernicla. The dominant coastal species were: Ciconiformes, Gruiformes and Charadriformes. Breeding waterbirds include: Egretta thula, Egretta tricolor, Egretta rufescens, Nicticorax nicticorax, Larus occidentalis, Sterna maxima, Falco peregrinus and Pandion haliaetus. The osprey colony is considered the world densest nesting population (180 breeding pairs). Among the raptors, other species include Buteo jamaicensis and Falco sparverius. Common upland species include Callipepla californica, Zenaida Macroura, Geococcyx californicus among others.

2, 4, 8, 24, 25, 26, 27, 28, 36
Fish A total of 172 species of fish were compiled from different sources, of these, 11 are sensitive species.

A 1993 study presented the first fish check-list for this area, 81 species of fish were recorded, some were drawn from analysis of the diet of seven species of fish-eating birds. In 1998 the 1993 check-list was updated, with the addition of 26 species, the current list includes a total of 107 species.

Another study in 1994, reported a total of 107 species of fish for Laguna San Ignacio and its environs. Of these, 12 species are considered as rare. The list also includes 34 species of temperate origin as well as 27 from the tropics.

4, 2, 29, 30
Benthic invertebrates A 1994 study reported a total of 244 species of invertebrates for Laguna San Ignacio and its environs. Ten out of these 244 species are considered as rare species. 4
Insect No information  
Other wildlife Two species of amphibia, 37 of reptiles (21 are sensitive species), and 46 species of mammals (8 are sensitive species and two are introduced) have been reported for the area by a 1994 study. Amphibia are: Bufo punctatus and Scaphiopus couchi. The most conspicuous reptile in the area include: Callisaurus draconoides, Phrynosoma coronatum, Dipsosaurus dorsalis, Masticophis flagellum, Pitouphis melanoleucos, Salvadora hexalepis Crotalus ruber and others. Among mammals the dominant species include some bats such as Myotis californicus, Pipistrelus hesperus and Eptesicus fuscus, but also Canis latrans, Lepus californicus, Procyon lotor, Dipodomys peninsularis and Dipodomys merriami, Ammospermophilus leucurus, Antilocapra americana, Odocoileus hemionus, although the last two species are rather rare, they augment the biological importance of the site.

A 1990 study, estimated 300-400 gray whales (Eschrichtius robustus), in the lagoon.

The adjacent area to Laguna San Ignacio is part of the historical distribution range of the peninsular pronghorn (Antilocapra americana peninsularis), and although this area is not longer considered part of the current range, on 27 May 1992 a couple of pronghorns were sighted near the area known as El Medano Amarillo, northeast of the lagoon.

4, 8, 32, 33, 34
Special status species Cooper´s hawk (Accipiter cooperii), Sharp-shinned hawk (Accipiter striatus), Northern pintail (Anas acuta), American wigeon (Anas americana), Blue-winged teal (Anas discors), Greater white-fronted goose (Anser albifrons elgansi), Golden eagle (Aquila chrysaetos), Short-eared owl (Asio flammeus), Lesser scaup (Aythya affinis), Cattle egret (Bubulcus ibis *), Zone-tailed hawk (Buteo albonotatus), Red-tailed hawk (Buteo jamaicensis), Costa´s hummingbird (Calypte costae), Great egret (Casmerodius albus), Northern harrier (Circus cyaneus), Tundra swan (Cygnus columbianus), Snowy plover (Charadrius alexandrinus), Reddish egret (Egretta rufescens), Horned lark (Eremophila alpestris), Merlin (Falco columbarius), Praire falcon (Falco mexicanus), Peregrine falco (Falco peregrinus), American kestrel (Falco sparverius), Bald eagle (Haliaetus leucocephalus), cliff swallow (Hirundo pyrrhonota), Barn swallow (Hirundo rustica), Xantus' hummingbird (Hylocharis xantusii ), California gull (Larus californicus), Heermann s gull (Larus heermani), Long-billed curlew (Numenius americanus), Ashy storm-petrel (Oceanodroma homocroa), Black storm petrel (Oceanodroma melania), Western screech-owl (Otus kennicottii), Osprey (Pandion haliaetus), brown pelican (Pelecanus occidentalis californicus), Double-crested cormorant (Phalacrocorax auritus), Crested caracara (Polyborus plancus), Pink-footed shearwater (Puffinus creatopus), Black-vented shearwater (Puffinus opisthomelas), Clapper rail (Rallus longirostris), Northern waterthrush (Seiurus noveboracensis), Burrowing owl (Speotyto cunicularia), Least tern (Sterna antillarum browni), Elegant tern (Sterna elegans), Common barn owl (Tyto alba). Sensitive plant species include: Sand verbena (Abronia gracilis), Beach sand verbena (Abronia maritima), Ragweed Ambrosia (Franseria) magdalena, Rattleweed (Astragalus fastidius), Salt bush (Atriplex julacea), Maritime hedhehog (Echinocereus maritimus), Palmer´s frankenia (Frankenia palmeri), Sour pitaya (Machaerocereus (Steneocereus) gummosus)), Elephant tree (Pachycormus discolor var. veatchiana), Parish´s Glasswort (Salicornia ( Arthrocnemum) subterminalis), Climbing milkweed (Sarcostemma arenarium), California cordgrass (Spartina foliosa), Estuary sea-blite (Suaeda esteroa), Agave vizcainoensis, Atriplex leucophylla, Bouteloua annua, Camissonia cardiophylla subsp. cedrosensis, Camissonia crassifolia, Dithyrea californica var. clinata, Dyssodia anthemidifolia, Lotus bryantii, Encelia ventorum, Eriogonum intricatum, Nama demissum, Nicolletia trifida, Spharalcea fulva. Other sensitive fauna are peninsular pronghorn (Antilocapra americana), Gray whale (Eschrichtius robustus), Elephant seal (Mirounga angustirostris), Harbour seal (Phoca vitulina), Badger (Taxidea taxus), Desert Kit Fox (Vulpes macrotys), and California sea lion (Zalophus californianus) 35
OUTLOOK   SOURCE
Enhancement status The management plan of the Biosphere Reserve El Vizcaino establishes the actions, strategies and rules that are needed to achieve the conservation of the natural areas and resources of this protected area. Local people have been trained as nature guides and some NGO have been developing environmental education and community development programs for the local communities. Ecotourism and aquaculture are the two most sustainable economic activities in the area.  
Watershed management None  
Pressure Temporal or movil fishermen camps lacking of the most basic services are built on the margins of the lagoon by using wood, old vehicles and other junk. These camps are abandoned after one or several fishing or clamming seasons, along with large amounts of trash, shells and other fishing subproducts. Unintentional introduction of dogs and cats into the islands. Uncontrolled human settlements along the margins of the lagoon (including fishermen and tourist camps), especially in the narrow Esteros El Cardon, El Delgadito and El Datil, along the lack of basic sanitary services represent habitat encroachment, pollution sources and are detrimental to the landscape and to the ecosystem health. A saltwork company is planning to build a huge (more than 52,000 ha) solar salt evaporation pond system at the natural saltflats, located at the northern end of Laguna San Ignacio, which it would change the landscape of this relatively pristine wetland. This planned industrial development would be within the buffer zone of the Biosphere Reserve El Vizcaino and also includes the construction of a wharf.

Bird and whale-watching activities are regulated but no enforced.

 


Back