Quantitive Ecology
Biodiversity is defined as the diversity of beings and
things that related to the environment such creatures. Diversity includes two
levels:
1. Genetic diversity, a diversity that
is the best, because this diversity can continue and be lowered. Genetic
diversity is associated with distinctive ecological and evolutionary processes.
2. Diversity of species, including
flora and fauna. Diverse types of behavior, life strategies, shape, chain food,
space and also the dependence between the type of one another. The existence of
high diversity will produce a steady environmental stability.
The diversity of species is also called the
heterogeneity of types, is a unique characteristic to describe the community
structure in the organization's life. A community is said to have high species
diversity, if the abundance of each kind of high and low species diversity
conversely if only tar-be some kind of abundance.
Diversity index can be used to express the abundance of species
in a community relations. Diversity consists of two components namely:
1. The total number of species.
2. The similarity (How abundance of data spread across many
species).
Species richness, evenenness, and diversity
a. Species richness
of species richness is the number of species in the area in a
community, each species does not seem to have the same number of individuals.
b. Shareable individuals
between species called fairness or equibility species. Equity to a maximum if
all species have the same number of individuals.
c. Species diversity is a
combination of richness and evenness. Species diversity is species richness in
species evenness, and there is a formula to express a single index number.
Biologically, diversity is the heterogeneity of the population of a community.
B. Some species diversity index
Diversity index used to determine the
biodiversity of organisms studied. In principle, the higher the index value,
meaning it is increasingly diverse community waters and not dominated by one or
more of the taxon there. Generally, this type of calculation for plankton
diversity index Simpson formula used, and for benthos is Shannon & Wiener.
Based on the formula calculation results aquatic biota diversity index, it is
known generally about the biological status of water quality. Criteria for
plankton, when the Simpson diversity index is less than 0.6, indicating that
there has been a perturbation (disruption) of the water quality of the life of
plankton (Odum, 1975). The main factors affecting the number of organisms, the
species diversity and dominance among others, the destruction of natural
habitats such as land conversion, pollution and organic chemistry, as well as
climate change (Widodo, 1997).
1.
Richness
index
of
species richness index (S), which is the total number of species in a
community. S
depending
on the sample size (and the time required to achieve it), this is limited as a
comparative index. Therefore, it is proposed to calculate the index number of
species richness which depends on the sample size. This is because the
relationship between the S and the total number of individuals was observed,
which increases with increasing sample size.
2.
Diversity
index
Richness
species and similarity within a single value is described with Deversitas
index. Diversity index may result from a combination of species richness and
similarity .There same diversity index values obtained from the community with
a richness of high similarity is low and if a same community obtained from
communities with high richness and low similarity. If the only value diversity
index, it is impossible to say what relative importance of species richness and
similarity. more easily ecologically
NA = S (Pi)1 / (1-A)
where
Pi = the size of the individual (or biomass, etc.) that are owned by a single
species. indicates that the sequence 0, 1, and 2 of the amount of diversity.
Number of
Diversity:
Total
0: N0 = S where S is the number of total species
number
1: N1 = e H 'where H is the index Shanon
Number
2: N 2 = 1 /ë where ë is
the index of Simpson.
This
diversity in the number of units, the number of species counted was named by
Hill
as
the effective number of species present in the sample. The effective number of
species
is
a matter for the comparable abundance distributed among
species.
More specifically, N0 is the number of all species in the sample (without
regard
to their abundance), N2 is the number of species is most abundant and N1 is the
number of species is abundant (always between N0 and N1 N2). In other words,
the effective number of species is a count of the number of species in the
sample where each species is affected by the richest. Example: the sample with
11 species and 100 individuals where abundance is dispersed as 90, 1, 1, 1,1,
1, 1, 1, 1, 1, 1. Only one species is very abundant, allegedly N2 close to 1
(N2 = 1 , 23). N0 = 11 and N1 = 1.74. So the unit Hill, s is a species whose
numbers rose: 1) less than the width occupied by rare species (called N0, the
lowest number, is the number of all species in the sample), 2). The lower value
resulting from the N1 and N2, showed abundant and very abundant in the sample.
There
are two indices are required to complete the diversity Hill:
1. Simpson index
l = S Pi2
Where:
Pi is the abundance of each species proporsial with
Pi
= ni, i = 1, 2, 3,. , , , 5 where ni is the number of individuals on that
species,
N
is the total number of known inidividu for all S species in the population
index value is from 0-1 indicating the possibility that two individuals taken
at random from a population of the same species. If the probability is high
that the 2nd individual has the same species, the diversity of the community
that the sample is low.
2. Shannon Index
This
index is based on information theory and an average count
of
uncertainty in predicting what species were selected randomly from the
collection of species and individual S N will be held. This average rose with
increasing number of species and individual distribution among species-species
become equal / equitable. There are two things that are owned by Shanon index,
namely;
1. H '= 0 if and only if there is one species in the sample.
2. H is the maximum only when all the species S is
represented bynumber of
the
same individuals, it is the abundance of equitable distribution perfectly.
3.
Similarity
index
If
theall species in a sample of the same abundance, it indicates that the maximum
similarity index and will decline toward zero as the relative abundance of a
species that is not the same. According Hurlbert (1971)
has
an abundance of ownership if they can be represented more.
V '= D
_____
Dmax
where
D is the diversity index, while dmin and Dmax arevalue
the
minimum and maximumin a sequence that D can be obtained. For the
treatment
of similarity index refers to the study of Alatalo (1981). Similarity index
(E1). Generally similarity index used were:
E1 = H '= ln (N1)
__________
Ln (S) ln (N0)
This
is almost the same as the formula J' by Pielou (1975, 1977), where H 'relatively
quickly obtained the maximum value that H 'is obtained when all the species in
the sample without error even with one individual per species (ie ln S).
C. Equibility index and dominance
the species diversity index (H ') describes the state of a
population of organisms mathematically, to make it easier to analyze the
information the number of individuals of each species in a community. Among
these species diversity index is the diversity index Shannon - Wiener.
There are two general diversity index,
1. Equibility index: the
index homogeneity / equalization
2. Dominance index: the
index most widely / general
dominance index is used to obtain information about the types of
fish that dominate in a community in each habitat index Dominance proposed by Simpson that (Ludwig and Reynolds,
1988):
C = Σ( )²
With C = Index dominance Simpson
S = Number of types (species)
ni = the total number of individual types of i
N = total number of individuals in total n
Pi = ni / N = as a proportion of all i
Values dominance index close to one (1) if the community is
dominated by a certain type or species dominance and if the index is close to
zero (0) then no species or species that dominate Odum (1971). Many say the
least species are present in a water sample will affect the dominance index,
although this value depends on the number of individuals of each species
(Kaswadji, 1976).
The influence of environment on the quality of fish abundance is
always different depending on the type of fish, because each species of fish
have different adaptation and tolerance to habitat. The index is used to obtain
more detailed information about fish communities (Anwar, 2011). Comparison
between diversity and maximum diversity expressed se-like uniformity of the
population, which is symbolized by the letter E. The value of this E-sar Berki
between 0 - 1. The smaller the value E, the smaller the uniformity of the
population, meaning that the spread of the number of individuals of each
species are not the same and there is a tendency of the species to dominate,
and vice versa greater the value of E then there is no dominant species. To see
the dominance of a species used dominance index (C).
Based on the value of diversity zoobentos index, which is
calculated based on the formulation of Shannon-Wiener, may be determined some
water quality. Wilhm (1975) states that the water is heavily polluted, the
zoobentos species diversity index less than one. If the range between one and
three, then the half-contaminated water. Clean water, large the zoobentos
diversity index of three. Staub et al. in Wilhm (1975) stated that based on the
diversity index zoobentos, water quality can be grouped into: heavily polluted
(0 <H '<1), half polluted (1 <H' <2), lightly polluted (2 <H
'<3) and polluted very light (3 <H <4.5). The range of values of H
'that come into one's vision-right part of the water quality assessment carried
out in an integrated manner by a factor of chemical physics of water.
Meanwhile, Lee et al. (1978) states that the value of the diversity index (H)
in waters heavily polluted, less than one (H <1), polluted medium (1.0 to
1.5), lightly polluted (1.6 to 2.0), and H polluted not greater than two (H>
2.0).
To get an idea of the relationship between physical and chemical
factors and community structure of macrozoobenthos done using regression
analysis. More detailed analysis can be done with the "principle
components analysis". From these figures are expected to be disclosed
types of macrozoobenthos alleged can be used as an indicator of water quality
as well as any chemical physics factor that primarily affect the existence of
macrozoobenthos in the waters.
The
higher the index of dominance then the diversity kind of a diminishing habitat
and vice versa. Level or index of
dominance and diversity of new habitats because they good enough dominance
index level or less while high diversity index.
The
level of diversity of the habitat shows fertility rates of these habitats. The
fertility of a habitat greatly affect the bio-diversity community
D. Richness species
Richness
much size a bit of diversity in an animal species
are present in a place of life in a certain time. It - it is influenced by
several factors, including:
1.
Reproduction
2.
Food
3.
Availability
4.
Adaptability
5.
The number of predators
Refrences:
Deshmukh, Lan, 1986. Ekologi dan Biologi Tropika. Blackwell Scientific Publications Limited, Oxford.
Erawati, Nety V., dan Sih Kahono (2010). “J. Entomol. Indon” Keanekaragaman Dan Kelimpahan Belalang Dan Kerabatnya (Orthoptera) Pada Ekosistem Pegunungan Di Taman Nasional Gunung Halimun-Salak. September 2010, Vol. 7, No. 2. Hal: 100-115.
Indriyanto, 2010. Ekologi Hutan. Bumi Aksara, Jakarta.
Michael, P., 1999. Metode Ekologi Untuk Penyelidikan Ladang Dan Laboratorium. Universitas Indonesia Press, Jakarta.
Soegianto, A., 1994. Ekologi Kuantitatif:Metode Analisis Populasi dan Komunitas. Penerbit Usaha Nasional, Jakarta.

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BalasHapus