FOREST REGENERATION PROJECT

 

OMERE WIKI is an Ecuadorian based environmental group currently seeking status as a Foundation.

In this proposal funding is solicited for the initial stages of the El Chaco Project. This is the establishment of a tree nursery for reforestation of the 15 hectares which currently comprise the reserve, the employment of a permanent warden who will maintain the tree nursery and carry out the reforestation work. The nursery will be producing plantable trees in about a year after it has been established. However a portion of the reserve is suffering from soil erosion and requires immediate reforestation. We thus also seek funding for the purchase and planting of tree seedlings.

The longer term aims of the project, which are to preserve and reforest the entire El Chaco valley, an area of about 100 hectares, are also outlined.

INTRODUCTION

THE EL CHACO VALLEY

HISTORY

CLIMATE

FAUNA AND FLORA

MAMMALS

BIRDS

REPTILES AND AMPHIBIANS

FLORA

ENVIRONMENTAL IMPACTS

PREVIOUS REFORESTATION WORK

REFORESTATION PROGRAMME

FUTURE AIMS

BUDGET

ELCHACO UPDATE 3/10/97

 

 

1 INTRODUCTION

Ecuador is one of the most biologically diverse countries in the world. Comprising only 0.1% of the planet's land area, contains 10% of the worlds plant species. Ecuador has 3,500 orchid species, more than any country in South America, including that of  Brazil, which is many times larger. Ecuador has the sites with the largest known reptile and amphibian fauna, and the Rio Napo in the Ecuadorian Amazon has 473 fish species, more than any river system of comparable size.
 
Ecuador's conservation record however is poor. Only 8% of the forest on the western Andean slopes was estimated to exist in 1992. This forest, part of the Choco Biological Region, was one of the richest forests in the world. Probably considerably less than this 8% exists today. The Ecuadorian Amazon has fared somewhat better, with about 60% of forest cover remaining, though the continuing uncontrolled influx of colonists along oil access roads makes the long term prospects poor, even in supposedly protected areas such as Yasuni National Park.
 
The native vegetation of the Inter-Andean basin however has now been practically eliminated, being replaced by cultivation and plantations of Eucalyptus. Even on the mountain slopes which are apparently uninhabited, there are no trees. Here forest regeneration is prevented by constant deliberate burning.
 
The inter-Andean environment is now in a state of deterioration. Annual droughts of increasing intensity threaten agriculture and the viability of hydroelectric schemes. That a dramatic decline in environmental quality is occurring is attested by the virtual disappearance of once common species of frogs in the genera Atelopus and Colostethus from the Andes in the last ten years.
Fragments of Andean forest however still remain in privately run reserves such as Guandera in the north, Mazan in the south and closer to Quito in the Pasachoa reserve.
 
Of considerable interest is that considerable patches of native forest were found to remain in the El Chaco Valley. Being at a lower elevation, about 2,400m from the above mentioned reserves, the fauna and flora of El Chaco may prove to be distinct and thus represent a habitat type which is even more endangered. Fieldwork has only just started in El Chaco, but already there is evidence that the forest is distinct. 1) The presence of Sangre de Drago (Croton sp.), a tree which occurs on the Western and Amazonian slopes of the Andes, and previously not known from the Inter-Andean Valley. 2) the presence of the bird Unicolored Tapaculo, which also normally inhabits the Western and Amazonian Andean slopes, but not the Inter-Andean Valley.
 
As well as preserving a habitat type that has virtually disappeared, the El Chaco project aims set an example as an attempt to reverse the environmental deterioration that has occurred in the Sierra. By propagation of the species which remain in the forest patches in El Chaco, we hope to restore the native forest to the entire valley.

 

2 THE EL CHACO VALLEY

The El Chaco Biological Reserve lies in the El Chaco Valley on the north-west slope of Ilalo, a mountain of volcanic origin near the town of Tumbaco, about half an hours drive from Quito. The reserve currently consists of two properties in private ownership, one of 10 hectares and one of 5 hectares. However ultimately we hope to purchase the remaining properties in the valley, approximately 100 hectares.
 
The El Chaco valley lies at about 2,400m altitude and consists of a wide U shaped valley with a stream running in a steep gorge in the valley bottom. The gorge is densely forested and forms the main reserve of native species which formerly would have inhabited the entire valley. Running down the valley sides are shallower ravines. Many of these are also forested. At the head of the valley there is a considerable portion of primary forest remaining, about 10 hectares in extent. The greater part of the valley, especially the steeper slopes, however consists of a species poor grassland in which forest regeneration is prevented by grazing and by fire.
 
Ilalo is designated an Ecological Reserve by the Municipality of Quito. However this designation affords little real protection. However this designation prevents urban development as it is prohibited to sell lots of less than 5 hectares in area.

 

3 HISTORY

Ilalo is the site of the oldest human settlements in the Quito area, dating back about 10,000 years. Obsidian flakes, used as cutting tools by these cultures, are frequently found in the valley, where they have been exposed on eroded soil surfaces. A few pottery fragments, from later cultures, have also been found.
 
According to local resident Manuel Walichico, the upper part of the valley was densely forested about 40-50 years ago, with big trees more than 2 metres in diameter. The valley was part of Hacienda La Vina, which during the agricultural reform, was divided among the former workers, now organised in the Communa L.N. Chavez. Since then some of these properties have been sold on, including the two which now comprise the biological reserve.

 

4 CLIMATE

Weather records began in May 1997. During this month minimum temperatures ranged from 10.5 to 15 C and maximum temperatures from 15 to 22.5 C. The rainfall for May was 83mm. Rain falls throughout the year except for a dry season from June to September. Morning mists, even during dry spells, would indicate that cloudforest vegetation may have previously existed on the now deforested higher slopes.

 
The majority of the rainfall falls as intense cloudbursts in which more than 20mm may fall in a short time. Because the valley sides are largely deforested, this rainfall is channeled rapidly down ravines on the valley sides to the river. These ravines thus only flow with water during and immediately after heavy rain. Although the main river flows throughout the year, it is subject to extreme floods. Reforestation of the valley sides will thus be essential for the regulation of the hydrology of the valley.

 

5 FAUNA AND FLORA

Only preliminary studies have been carried out to date, and most of this section is based on casual sightings. It is however intended to circulate updates to the species lists given below as further studies are carried out. We hope that in circulating this proposal, biologists will be stimulated to visit the reserve.

 

5.1 MAMMALS

Among the mammals rabbits (Sylvivagus brasiliensis) and Paramo fox are frequently seen in the area. There is also an unsubstantiated report of an ocelot with cubs seen five years ago.

5.2 BIRDS

The open areas of the valley sides support relatively few bird species which include Great Thrush, Rufus Crowned Sparrow and Eared Dove. However to judge from the calls heard, a rich bird fauna exists in the forest of the ravines and valley bottom. Most of this bird fauna remains unstudied but many of the calls heard are recognised as those inhabiting the forested Mazan reserve, near Cuenca. Of considerable interest was that Andean Condors are occasionally sighted in the valley. In September 1996, an immature individual was observed to alight briefly on the slope of the north east corner of the lower property and from July to August 1997 an adult individual was regularly sighted. As is usual for montane forest and sub-paramo habitats, there are many species of hummingbirds present. Also of considerable interest is that the Unicolored Tapaculo is present in El Chaco. This species occurs on the Western and Amazonian slopes of the Andes, and this may prove to be the first record from the Inter-Andean Valley. Croton seeds form a principal food source for the endangered Yellow Cheeked Parrot. According to ornithologist Francisco Sornoza, who is currently studying this species, the Croton trees of El Chaco would support a flock of this migratory species for about a month. This species occurs on the western slopes of the Andes, but it is not known yet if flocks visit El Chaco.

 

LIST OF BIRDS RECORDED FROM EL CHACO

CATHARTIDAE - VULTURES
Andean Condor Vultur gryphus
 
FALCONIDAE - FALCONS
American Kestrel Falco sparverius
 
COLUMBIDAE - PIGEONS, DOVES
Eared Dove Zenaida auriculata White-tipped Dove Leptotila verreauxi
 
TROCHILIDAE - HUMMINGBIRDS
Sparkling Violetear Colibri coruscans
Giant Hummingbird Patagonia gigas
Black-tailed Trainbearer Lesbia victoriae
 
FURNARIIDAE - HORNEROS, SPINETAILS ETC.
Azara's Spinetail Synallaxis azarae
 
RHINOCRYPTIDAE - TAPACULOS
Unicolored Tapaculo Scytalopus unicolor
 
TYRANNIDAE - FLYCATCHERS
Southern Beardless Tyrannulet Camptostoma obsoletum
TURDIDAE - THRUSHES, SOLITARES
Great Thrush Turdus fuscater
 
COEREBIDAE, HONEYCREEPERS
Black Flower-piercer Diglossa humeralis
 
FRINGILLIDAE - FINCHES
Rufus-collared Sparrow Zonotrichia capensis

 

5.3 REPTILES AND AMPHIBIANS
Reptiles and amphibians which have been recorded from the valley are as follows:
 
FROGS
Eleutherodactylus unistrigatus
 
LIZARDS
Pholidobolus montium Stenocercus sp.
 
SNAKES
Liophis sp.

Suprisingly no Gastrotheca have been heard calling, although it is likely that this species may exist higher up in the valley. Species of Colostethus and Atelopus may have inhabited the valley previously, but these species have become extinct or rare throughout the Andes in recent years. Nevertheless they should be looked for in the forest patches higher in the valley.

 

5.4 FLORA

The vegetation consists of forest and scrubland in the ravines and in the valley bottom, while the valley sides are largely deforested and consist of a species poor grassland. Higher up in the valley however more extensive areas of scrub and forest extend up the valley sides. The limited studies carried out to date suggest that the fauna and flora of El Chaco may prove to be distinct from nearby reserves such as Pasachoa. El Chaco is at a relatively low altitude compared to other protected Andean forest remnants and thus may represent a habitat class which is even more endangered. The most notable feature of the El Chaco forest is the presence of a species of Sangre de Drago tree (Croton sp.) (Plate 1 d). Sangre de Drago is known from the Oriente (the Ecuadorian Amazon) and from the western slopes of the Andes. However there were no previous records from the Inter Andean Valley. The El Chaco Croton resembles the species which grows on the Pacific slopes of the Andes, although it is possible that it may prove to be an undescribed species. Sangre de Drago produces a red latex which has medicinal properties, and products are currently undergoing medical trials in the USA.

Probably the greater part of the forest is secondary in origin, to judge from the relatively small size of the trees. The dominant tree in the higher and more humid reaches of the valley is Croton. Large trees, and remnants of the original primary forest, however occur on the more inaccessible slopes in the upper reaches of the valley.

The ravine in the valley bottom is virtually unexplored, being only accessible in a few places. Due to inaccessibility, the flora has probably been little affected by human activity. Being perpetually humid, the ravine has a rich flora of mosses, ferns and gesneriads, and the trees are hung with mosses, lichens, ferns and bromeliads. Lower in the valley there are many bare rocky cliffs. These are clothed with lithophytic vegetation such as the bromeliads Pitcairnia and Tillandsia and the orchids: Pleurothallis and Epidendrum. The list of plant species given below is very preliminary and is based on photographs identified in the National Herbarium, Quito.

 

LIST OF PLANTS RECORDED FROM EL CHACO

ASTERACEAE
Barnedesia arborea
 
BROMELIACEAE
Pitcairnia sp. Puya sp. Tillandsia sp (1) Tillandsia sp. (2) Tillandsia sp. (3) Tilandsia sp. (4)
 
CAMANULACEAE
Centropogon sp. Salvia pichinchensis
 
GESNERIACEAE
Heppiella sp.
 
LAMIACEAE
Minostachys mollis
 
ORCHIDACEAE
Altenstenia sp. Epidendrum sp. Pleurothallis sp.
 
POLYGALACEAE
Monninia obtusifolia
 
RUBIACEAE
Arcitiphilum tinifolium
SCROPHULARIACEAE
Calceolaria sp. (1) Calceolaria sp. (2) Calceolaria sp. (3)
 
VERBENACEAE
Duranta triacantha
 

6 ENVIRONMENTAL IMPACTS

The environmental change due to human activity varies along the length of the valley, being great near the valley mouth, and considerably less at the head of the valley. The lower reaches of the valley have been deforested for a long time, probably many centuries, and are devoid of natural vegetation. In this zone the soils are badly eroded, the topsoil on the valley sides has been lost, revealing a compact nutrient poor clay. Erosion in this zone has been compounded because some of the property owners have sold topsoil by the truckload to nearby brickworks.

Further up the valley, at the commencement of the lower property, soil erosion has been much less, the underlying clay is exposed only in a small area on the slope in the north western corner of the lower property. Nevertheless soil erosion remains a problem, during heavy rains landslides are frequently observed on the deforested valley sides. Erosion is occurring on the slope at the southern end of the lower property, this area is in need of immediate reforestation and is discussed in more detail below. Travelling further up the valley the climate becomes noticeably more humid, the vegetation richer and problems of soil erosion less.

While impacts from agriculture in the valley are relatively low, only small extensions of land are cultivated for maize, beans etc., and currently few cattle and horses are grazed, the main impact on the vegetation has been from deliberate burning. It is fire, rather than any other activity, which has prevented forest regeneration in the area. During the dry season from June to October, fires rage on the mountain slopes and trees that have taken decades to re-establish are wiped out in a few hours.

One of the property owners in the valley has planted an area of about 15 hectares with Eucalyptus. This is by far the most commonly used tree for reforestation in Ecuador. This tree grows rapidly and gives a quick yield of timber, however does little to protect the soil. Its intense demand for water dries out the soil and toxins in the leaf fall suppress the native vegetation.

 

7 PREVIOUS REFORESTATION WORK IN EL CHACO

Attempts have been made to reforest the two properties which comprise the reserve for the past ten years, but with varying degrees of success. Firstly, in spite of the considerable propaganda produced at that time by organisations such as MAG (the Ecuadorian Ministry of Agriculture), the Municipality of Quito, Fundacion Natura and also by foreign based aid organisations, it was very difficult to obtain native species at affordable prices for reforestation, or even for that matter alien species, other than Eucalyptus. The first reforestations were carried out with alien species, Pinus radiata and Cupressus, and later on with the few native species available such as Aliso, Chaulan, Jacaranda, Acacia, Capuli and alien broad leaved species as Grevillea, Callistemon etc. These trees were obtained from the government run MAG and INIAP nurseries, which unfortunately now do not exist.

In spite of logistical problems, in that the trees had to be brought in on horseback, as there was no access road to the valley at that time, the greater part of the pastures of the two properties were planted with trees. Success however was limited because many of the trees were destroyed by fires started deliberately on the neighbouring properties. Nevertheless there were certain successes. The Cupressus windbreak along the northern boundary of the lower property (Plate 3 b) is nearly completely intact, the tallest now reaching more than 3m in height. The establishment of this windbreak will facilitate the establishment of more sensitive native species behind. A paddock in the north western corner of this property which is suffering from soil erosion was successfully established with Guaba (Inga sp.) This native leguminous tree is ideal for regeneration of eroded grasslands. The tallest individuals now reach 2m in height and their nitrate rich leaf fall is starting to modify the soil structure. One of these trees is illustrated in Plate 3 a.

Isolated trees, some of which surpass 1m in height, have survived on the slopes. Many Callistemon (Australian bottle brush) trees have survived. Although these are not native to Ecuador, they were deliberately chosen because they are easy to establish and form an important source of nectar. Some of the larger individuals are now constantly in flower and attract many species of hummingbirds.

Trees have fared rather better on the upper property, where there are many pines now exceeding 3m in height.

 

8 PROPOSAL FOR CONTINUATION OF THE REFORESTATION PROGRAMME

A) ESTABLISHMENT OF TREE NURSERY
Because of the difficulty in obtaining native species for reforestation and the limited range of species available, we have decided that the most economical means of reforesting the reserve will be by establishing our own tree nursery. This nursery is also essential because we plan to propagate primarily species already occurring in the valley, rather than use the limited range of native species commercially available, which, apart from being expensive, many may not have occurred naturally in the valley. In the future we also plan to make trees available to the general public, given that in spite of the considerable publicity given to reforestation in Ecuador, it is very difficult to obtain any species other than Eucalyptus and pine.

This tree nursery will be primarily for propagation of species which are native to the valley, our genetic resource being the forest remaining in the valley bottom. In this way we aim to restore an authentic native forest to the valley sides. It is probable however that many species which previously occurred here have become extinct and we may also consider propagating species from nearby forests such as Pasachoa. Some tree species are now represented by only a few remaining individuals which grow in inaccessible areas on the valley slopes or in the bottom of the ravine. Serious expeditions will have to be mounted to reach these specimens.

Much of this work will be experimental in nature, establishing a methodology for propagation of these species. In many cases seeds can be gathered and germinated, and others may be propagated by cuttings. The young trees will be grown on in plastic bags until large enough to be planted. Some species may be difficult to germinate. This is the case with the only individual of Chinchinal (a species of Acacia) we have found in the valley. No seeds that we have planted have germinated. However careful weeding around the base of this tree has promoted a dense growth of seedlings which later can be transferred to pots. Sangre de Drago (Croton) seeds are relatively easy to collect, although very few seedlings of this species have been seen in the valley. Priority will be given to increasing the forest cover of this species.

In addition to trees, it will be important to establish species capable of controlling soil erosion. In nearby forests such as Pasachoa, a bamboo of the genus Chusquea is one of the first plant species to regenerate forest clearings caused by landslides. This bamboo quickly establishes a continuous mat of vegetation which prevents further soil movement. Chusquea has probably been eliminated from El Chaco due to fire. The reintroduction of this species will be desirable for the stabilisation of soil in the ravines running down the valley sides and thus form the first stage in succession to climax forest.

Some areas of the two properties are currently grazed by horses and llamas. However it is not intended to eliminate grazing animals entirely from the reserve as the maintenence of grazed areas will be essential to act as firebreaks. The creation of a mosaic of forest and pasture will help to minimise damage to the forest in the case of fire in the dry season. While single trees can be planted in these pastures (protected by fences while young), it is intended to regenerate a continuous forest canopy and understory in the ravines and on the valley sides.

B) CONTROL OF SOIL EROSION
The tree nursery will be producing plantable trees from about a year after it has been established. However one area of the reserve requires immediate planting to prevent further soil erosion. This is the southernmost gully on the lower property (Plate 3 c and d). During heavy rain in the previous (1986) wet season a considerable landslide of rocks and soil was washed down this gully. This problem was compounded because of a fire three years ago which destroyed the forest in the lower portion of this gully. Although considerable regeneration has occurred since from stump sprouts, immediate reforestation is required to prevent further erosion. It is proposed to fence this area off from grazing animals and plant the area with fast growing native leguminous species: Inga, Jacaranda and Acacia. Later on, this area can be interplanted with trees produced by the tree nursery, such as Croton.
 
C) EMPLOYMENT OF PERMANENT WARDEN
In view of the problems that have occurred in the past because of fire, the employment of a warden who will live on site and patrol the properties is essential. The warden will also maintain the tree nursery and carry out replanting work.
 
D) BIOLOGICAL STUDIES
It is hoped to commence preliminary biological studies this year. While these studies will mainly be carried out by volunteers and by visiting biologists, we seek funds to pay expenses, and also for the fees charged for drying and identifying plant specimens in the National Herbarium, Quito.

 

9 FUTURE AIMS OF THE EL CHACO PROJECT

While the current proposal is to preserve the forest and to reforest the cleared areas of two properties, totalling 15 hectares in the El Chaco Valley, it is hoped to greatly extend this project in the future. We intend to seek funds to purchase and preserve the remaining land in the valley. This land will be owned and administered by an Ecuadorian based foundation which is currently being established. Purchasing approximately 100 hectares of land, will enable the entire watershed of the valley to be preserved. At the head of the valley, the forest is considerably more intact, having suffered less from human interference. It is not intended however to purchase properties in the lower part of the valley, below the northern boundary of the lower property, as this land is severely degraded and has little conservation value.

It is hoped to work directly with the Municipality of Quito, who has already designated the area as an Ecological Reserve. As Quito continues to expand into the Tumbaco valley, there will be a greater need to retain and restore natural areas such as El Chaco. Being situated close to Quito, reached in half an hour by car, there is great potential for establishing educational facilities in order to promote the need for conservation, the establishment of a botanical garden and demonstration models of more sustainable forms of agriculture based on the Permaculture system. El Chaco will be the nearest and most accessible forest reserve to Quito.

We also hope to attract researchers from foreign and Ecuadorian universities as the reserve will offer a great opportunity to investigate and develop methods of forest regeneration. It will also be important to maintain an ongoing programme of fauna and flora monitoring as it will be of considerable interest to document the extent of recovery of biodiversity as tree cover is re-established in the valley.

 

10 BUDGET

This budget is for the first two years of the reforestation programme

A) EMPLOYMENT OF PERMANENT WARDEN
Salary $150 per month for two years $3600
 
B) TREE NURSERY
This will be a simple structure, about 100m in floor area, constructed of wooden poles supporting a roof of shade cloth which will break the force of the sun and rain and prevent damage to the plants from the occasional hailstorm. The walls will be of transparent UV resistant plastic.

 

Materials:

Wooden poles (Eucalyptus) $500

Boards, for staging $450

UV resistant plastic $350

Shade cloth $450

Nails and wire $100

Transport of materials to site $100

Equipment for nursery:

Black plastic bags $200

2 Wheelbarrows $100

Miscellaneous, buckets, spades, pruners rooting powder etc. $200

 

Plant and seed collecting expeditions:

Logistic costs for seed and plant collecting expeditions (petrol, equipment etc.) $500

Labour: The work will be undertaken by the warden, however two labourers will be required for two weeks for construction of nursery $250

TOTAL $3,200

 

C) PURCHASE OF TREES FOR IMMEDIATE REFORESTATION WORK

Purchase or 1,000 trees (Inga, Acacia, Jacaranda) $1,500

Transportation to site $50

Fencing of gully (posts, barbed wire) $250

TOTAL $1,800

 

D) BIOLOGICAL PROGRAMME

Herbarium fees etc. $200

Food and transport for visiting biologists $400

 

TOTAL $600

 

GRAND TOTAL $9,200

This project has already received a donation of $700

 

TOTAL FUNDING SOLICITED $8,500

 

Dr. Morley Read
OMERE WIKI
Tel: 09 724161 Casilla 17-21-249
E-mail: mread@hoy.net