Study

Consequences of protection from grazing on diversity and abundance of the coastal lowland vegetation in eastern Saudi Arabia

  • Published source details Shaltout K.H., El-Halawany E.F. & El-Kady H.F. (1996) Consequences of protection from grazing on diversity and abundance of the coastal lowland vegetation in eastern Saudi Arabia. Biodiversity and Conservation, 5, 27-36.

Summary

Degradation of the rangeland is evident in many parts of Saudi Arabia as a result of a long history of overgrazing (mostly by camels and sheep), over-cutting, and many other anthropogenic factors. Protection against overexploitation may provide a chance for regeneration of vegetation in degraded areas, but regeneration attempts have been few in the Arabian Desert region. The present study was aimed at evaluating the possible recovery of vegetation as a result of protection from grazing and other exploitation at a coastal lowland site in eastern Saudi Arabia.

Study site: The study was undertaken at an experimental site (2.5 x 2.5 km), fully protected since 1980, near A1-Hassa Oasis, 20 km south-east of A1-Hufuf city in Al-Hassa region, eastern Saudi Arabia.

Vegetation sampling: Thirty-six blocks of 20 x 20 m were sampled to represent the prevailing (generally sandy) habitat and community variations inside (15 blocks) and outside (21 blocks) the protected area. In each, the following were recorded in spring 1993: species, species cover (using the fine-intercept method); and average height and diameter (based on measurements of 10 randomly selected individuals) of the dominant species, used a s a measure of plant size.

Species richness of the vegetation inside and outside the protected site was calculated as the average number of species per stand, and species turn-over as the ratio between the total number of species and the species richness. Relative evenness and concentration of dominance of species were calculated using Shannon-Weaver and Simpson indices, respectively, on the basis of the relative cover of species.

Soil sampling and soil analysis: In each block, soil samples were collected and soil texture (%sand/silt/clay) and organic matter were estimated. Soil-water extracts were prepared for the determination of electrical conductivity (i.e. as a measure of soil salinity) and pH measured. Determinations of concentrations of important soil nutrients potassium (K), calcium (Ca), sodium (Na), nitrogen (N), phosphorous (P) and magnesium (Mg) were made.

Vegetation: Eight plant communities were prominent in the study area, dominated respectively by Haloxylon salicornicum, Rhanterium epapposum, Seidlitzia rosmarinus, Panicum turgidum, Zygophylleum qatarence, Aleuropus lagopoides, Tamarix aphylla and Saueda aegyptiaca.

Compared to the area open to grazing, the vegetation inside the protected site had a higher numbers of total species (68 vs. 61), species richness/block (18.9 vs. 14.2), relative evenness (0.82 vs. 0.62) and total cover (66.5 vs. 39.7), but lower species turn-over (3.96 vs. 5.10) and relative concentration of dominance (0.28 vs. 0.38). The sizes of some of the dominant species (e.g. T.aphylla, S.rosmarinus, P.turgidum and S.aegyptiaca) were also significantly greater (frequently twice that) inside the protected area compared to individuals outside it.

The difference in total cover and plant size were thus especially marked; it should be noted that a visual estimation indicated that standing dead plant parts contributed, about 40% of the total cover inside the protected area and 20% outside.

Of 50 species of common occurrence, 26 contributed 88% of the total cover inside the protected area and 94% in the area open to grazing; 15 species had significantly higher plant cover, while only two (Frankenia pulverulenta and Kochia indica) had significantly lower cover, inside than outside the protected site.

Soil: Soil salinity and certain soil nutrients (N, K, Mg and Na) were significantly lower inside than outside (where presumably livestock droppings and urine enhanced nutrient availability) the protected area.

In conclusion, 14 years of protection against livestock grazing and human impacts led to recovery of vegetation.


Note: If using or referring to this published study, please read and quote the original paper, this can be viewed at:

http://www.springerlink.com/content/u103147kj8843562/fulltext.pdf

 

Output references
What Works 2021 cover

What Works in Conservation

What Works in Conservation provides expert assessments of the effectiveness of actions, based on summarised evidence, in synopses. Subjects covered so far include amphibians, birds, mammals, forests, peatland and control of freshwater invasive species. More are in progress.

More about What Works in Conservation

Download free PDF or purchase
The Conservation Evidence Journal

The Conservation Evidence Journal

An online, free to publish in, open-access journal publishing results from research and projects that test the effectiveness of conservation actions.

Read the latest volume: Volume 21

Go to the CE Journal

Discover more on our blog

Our blog contains the latest news and updates from the Conservation Evidence team, the Conservation Evidence Journal, and our global partners in evidence-based conservation.


Who uses Conservation Evidence?

Meet some of the evidence champions

Endangered Landscape ProgrammeRed List Champion - Arc Kent Wildlife Trust The Rufford Foundation Save the Frogs - Ghana Mauritian Wildlife Supporting Conservation Leaders
Sustainability Dashboard National Biodiversity Network Frog Life The international journey of Conservation - Oryx Cool Farm Alliance UNEP AWFA Bat Conservation InternationalPeople trust for endangered species Vincet Wildlife Trust