International Journal of Environmental & Agriculture Research (IJOEAR)
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
Faunistic Analysis of Soil Mites in Coffee Plantation
Patrícia de Pádua Marafeli1, Paulo Rebelles Reis2, Leopoldo Ferreira de Oliveira Bernardi3,
Pablo Antonio Martinez4
1
Universidade Federal de Lavras - UFLA, Lavras, MG, Brazil. Entomology Postgraduate Program.
Empresa de Pesquisa Agropecuária de Minas Gerais - EPAMIG Sul/EcoCentro, Lavras, MG, Brazil.
CNPq Researcher.
3
Universidade Federal de Lavras - UFLA - Departamento de Biologia/DBI – Setor de Ecologia Aplicada, Lavras, MG. Brazil.
CAPES / PNPD scholarship holder.
4
Universidad Nacional de La Plata, La Plata, Argentina.
2
Abstract ─ The soil-litter system is the natural habitat for a wide variety of organisms, microorganisms and invertebrates, with
differences in size and metabolism, which are responsible for numerous functions. The soil mesofauna is composed of animals of
body diameter between 100 μm and 2 mm, consisting of the groups Araneida, Acari, Collembola, Hymenoptera, Diptera,
Protura, Diplura, Symphyla, Enchytraeidae (Oligochaeta), Isoptera, Chilopoda, Diplopoda and Mollusca. These animals,
extremely dependent on humidity, move in the pores of the soil and at the interface between the litter and the soil. The edaphic
fauna, besides having a great functional diversity, presents a rich diversity of species. As a result, these organisms affect the
physical, chemical and, consequently, the biological factors of the soil. Therefore, the edaphic fauna and its activities are of
extreme importance so that the soil is fertile and can vigorously support the vegetation found there, being spontaneous or
cultivated. The composition, distribution and density of the edaphic acarofauna varies according to the soil depth, mites size,
location and the season of the year. Edaphic mites are generally found in greater quantities in the organic matter layer than in
the soil mineral. The subclass Acari is divided in seven orders being the Mesostigmata, Trombidiformes, Endeostigmata and
Sarcoptiformes those that frequently occur in the soil. In the order Sarcoptiformes the suborder Oribatida (formerly
Cryptostigmata) is one of the more numerous groups of soil arthropods, both in number of species and specimens. Considering
the above facts, it was the objective of this work to know the acarofauna of the soil in a coffee plantation and rank the taxa in a
decreasing way, by the use of faunistic analysis. The soil samples were taken in coffee plantation in the Experimental Station of
EPAMIG, in São Sebastião do Paraíso, MG, Brazil, in two periods, end of dry and end of rainy season of the year 2013, and the
extraction of edaphic mites of the soil mesofauna was done at the Laboratory of Acarology of EPAMIG Sul/EcoCentro, in
Lavras, as well as other activities related to the study. The result show that edaphic mites of the cohort Astigmatina and suborder
Oribatid are dominant in both periods studied, and can be worked to be an indicative of soil quality.
Keywords ─ Agricultural acarology, Coffea arabica, Edaphic mites, Soil mites, Soil mesofauna.
I.
INTRODUCTION
The edaphic fauna reflects the environmental conditions, and are the characteristics of habitat such as climate, soil type, amount
of accumulated litter, amount of organic matter, type of soil management, among others, which determine the groups of the soil
fauna that will be present and in what quantities [1].
The global knowledge of the richness of groups of soil organisms provides an indication of the ecological complexity of soil
communities [2] [3].
The soil-litter system is the natural habitat for a wide variety of organisms, microorganisms and invertebrates, with differences in
size and metabolism, which are responsible for numerous functions. The diversity of soil fauna is related to the great variety of
resources and microhabitats that the soil-litter system offers, a mixture of highly compartmentalized aquatic and aerial phases,
generating a mosaic of microclimatic conditions and thus favoring, therefore, a large number of associated functional groups [4]
[5].
Soil biota can be classified as: (1) Microfauna - composed of protozoa, nematodes and rotifers, whose diameter varies from 4 to
100 μm, which act indirectly in the nutrient cycle, regulating bacterial and fungal populations; (2) Mesofauna - which is
composed of animals of body diameter between 100 μm and 2 mm, consisting of the groups Araneida, Acari, Collembola,
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International Journal of Environmental & Agriculture Research (IJOEAR)
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
Hymenoptera, Diptera, Protura, Diplura, Symphyla, Oligochaeta, Isoptera, Chilopoda, Diplopoda and Mollusca, and can be
included small specimens from the Coleoptera order. These animals, extremely dependent on humidity, move in the pores of the
soil and at the interface between the litter and the soil. Among the trophic levels of this group, it stands out its significant
contribution in the regulation of the microbial population; (3) Macrofauna - composed of animals that present body diameter
between 2 and 20 mm and can belong to almost all orders found also in the mesofauna, except Acari, Collembola, Protura and
Diplura and including Annelida and Coleoptera. They are animals of great mobility and that play an important role in the
transportation of materials, both for making nests and burrows, and for building galleries that reach varying depths in the soil. Its
main functions are the fragmentation of the vegetal residue and its redistribution, the predation of other invertebrates and the
direct contribution in the structuring of the soil [6] [7].
Because they are sensitive and react to changes induced by natural phenomena to the soil and their vegetal cover, as well as by
anthropic activities, the populations and the diversity of the edaphic fauna can be used as bioindicators of the use of the soil or its
fertility, giving a notion of its current state and changes induced by internal and external forces (biotic and abiotic) over time.
Such disturbances alter the distribution of soil fauna as they alter the availability of food resources, modifying the intra and
interspecific ecological interactions. As changes in the environment, is cited for example, epigeous species, i.e., those that are
restricted to inhabit the topsoil, which are normally associated with the layer of litter, and therefore disappear with deforestation
or larger soil disturbances such as the use of plow and chemical products [8].
The edaphic fauna, besides having a great functional diversity, presents a rich diversity of species. As a result, these organisms
affect the physical, chemical and, consequently, the biological factors of the soil. Therefore, the edaphic fauna and its activities
are of extreme importance so that the soil is fertile and can vigorously support the vegetation found there, being spontaneous or
cultivated [9].
The edaphic mesofauna study has been directed to the evaluation of the influence of agricultural practices on its taxonomic units
as a whole, particularly to numerically more representative groups such as mites and springtails [10].
The study of these organisms initially consists of their capture, identification and quantification of the components of the
community in question. The literature found research that use different methods, adopted at the discretion of the researchers,
taking into account mainly the study objectives and the practical procedures. The most commonly used method is the extraction
of soil samples and subsequent removal of the organisms by use of collection funnel [11].
One of the used types of biological indicator of soil quality is the population monitoring of the edaphic mesofauna. Therefore, the
determination of the mesofauna is a biological indicator of the quality of the organic residues in order to contribute to the
evaluation of a soil management system [12].
Mites are members of the Arthropoda phylum, which comprise a vast array of terrestrial and marine invertebrates that share the
features of jointed legs and a chitinous exoskeleton. The mites belong to the large and diversified subphylum Chelicerata, where
the largest group is of the Arachnida class. The arachnids are terrestrial chelicerates, including the Acari subclass, which includes
mites and ticks, and which differs from the other arachnids by the absence of apparent segmentation [13].
The mites have as much diversity of food and way of feeding as of localities where they live. Regarding food habits, the variation
occurs even within each family, ranging from parasitic species of vertebrates and invertebrates to phytophagous and predatory
species [13].
The composition, distribution and density of the edaphic acarofauna varies according to the soil depth, mites size, location and
the season of the year [14 [15]. Edaphic mites are generally found in greater quantities in the organic matter layer than in the soil
mineral fraction [16].
The subclass Acari is divided in seven orders being the Mesostigmata, Trombidiformes, Endeostigmata and Sarcoptiformes those
that frequently occur in the soil. In the order Sarcoptiformes the suborder Oribatida (formerly Cryptostigmata) is one of the more
numerous groups of soil arthropods, both in number of species and specimens [17] [18] [13].
Considering the aforementioned facts, it was the objective of this work to know the acarofauna of the soil in a coffee and forest
plantation, as well as to classify by the use of faunistic analysis, in a decreasing way of occurrence, the found taxa.
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International Journal of Environmental & Agriculture Research (IJOEAR)
II.
2.1
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
MATERIAL AND METHODS
Study site
The study was accomplished at the Experimental Station of the Empresa de Pesquisa Agropecuária de Minas Gerais - EPAMIG
Sul, in the municipality of São Sebastião do Paraíso, MG, Brazil, in an already existing coffee plantation (Coffea arabica L.)
cultivar Paraíso with six years’ age, in the Dystroferric Red Latosol (Oxisol) soil type, in the spacing of 4.0 m between the lines
and 0.70 m between the plants, and in a neighboring forest in the same soil type.
2.2
Experimental design
The experimental design was in randomized block with eight treatments, being seven in the coffee plantation and the eighth
treatment in the forest, with three replications. The forest was an area located very close to the coffee plantation, with the same
type of soil, and constituted of a subperenifolia tropical native forest, having been used as a reference treatment of the type of soil
before the agricultural exploitation of the farm.
The samplings were made in 48 experimental plots, 42 in plots of coffee plantation and 6 in the forest, in each sampling period
that corresponded to the end of dry season and end of rainy season in the region of the study.
The coffee experimental plots consisted of four lines, 50 plants/line, and the useful part of the plot being composed of the two
central lines totaling 80 plants,40 plants/line, and the remaining other lines served as border.
2.3
Soil sampling
Two soil samplings, one at the end of the rainy season (June) and the other at the end of the dry season of the year in the study
region (October of 2013), were used to quantify the edaphic mites in the soil mesofauna.
The soil samples were extracted by means of a cylindrical probe made of stainless steel with 50 mm internal diameter and 53 mm
high (100 cm3), known as a cylinder for collecting not deformed soil samples (BRAVIFER - Indústria de Equipamentos e
Assessoria Agronômica Ltda. ME).
At each sampling time, two soil samples were extracted, one at 5 m from the beginning and the other at 5 m from the end of each
plot and every time in the central position between the lines of coffee plants. In the forest, the samples were taken also at each
sampling time and with the same cylindrical probe, 50 m from the border.
2.4
Extraction and identification of edaphic mites
The edaphic mites’ extractions of the soil samples were performed by means of Berlese-Tüllgren funnel extractor [19] [11]. In
the funnel, the samples were subjected to light and heat for seven days [20] to create a temperature and humidity gradient,
making the environment unfavorable for the organisms present, forcing them down until they fall into a collector vial containing
70% alcohol.
After being extracted, the mites were counted and removed from the alcohol of the collector vial with the use of a fine paintbrush and with the assistance of a binocular stereomicroscope at 40x magnification, and after were mounted on a microscopy
glass slide in Hoyer's medium and after being covered with a glass coverslip were identified with the use of a phase-contrast
binocular microscope.
The mites’ extraction from soil samples and their taxonomic identification were conducted in the Laboratory of Agricultural
Acarology of EPAMIG Sul/Research Center in Ecological Management of Pests and Plant Diseases - EcoCenter, in the city of
Lavras, Minas Gerais, Brazil.
The proposal presented by Lindquist, Krantz and Walter was used [13], with the elevation of suborder Endeostigmata to order, as
suggested by Pepato and Klimov [21]. In addition, in order to better visualize the results, the order Sarcoptiformes was split in
two groups, with the cohort Astigmatina [22] presented separately from the other species that belong to the suborder Oribatida.
2.5
Faunistic analysis
The obtained data were analyzed using the ANAFAU software, developed in the Department of Entomology, Phytopathology e.
Agricultural Zoology of the Luiz de Quiroz College of Agriculture/University of São Paulo, Brazil, recommended for great
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International Journal of Environmental & Agriculture Research (IJOEAR)
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
diversity of species [23] which allows to know the indexes of frequency, abundance, constancy and dominance of each taxon
found [24].
III.
3.1
RESULTS AND DISCUSSION
Soil samples from the end of rainy season
In the faunal analysis performed with soil mites collected at the end of the rainy season of 2013, the families Nanorchestidae
(Spelenorchestes sp.), Alycidae (Bimichaelia sp.), Eupodidae (Eupodes sp.1, sp.2), Rhodacaridae (Multidentorhodacarus sp.),
Tarsonemidae (Tarsonemus sp.), mites of the suborder Oribatida and hypopus phase (cohort Astigmatina, Family Acaridae,
genus Ryzopglyphus sp.) [22] (OCONNOR, 2009) were the ones that presented species or morphospecies considered to be
dominants (D), since they presented the maximum rates of faunistic classification, very abundant (ma), very frequent (MF) and
constant (W) during the period in which the study was performed (Table 1).
The suborder Oribatida was the one that presented the largest number of species, 20 species and morphospecies in four families
in the period. Of these, among others, the families Brachichthoniidae, Licnodamaeidae and the species Galumna flabellifera,
Berlezetes brasilizetoides, Sherolibates sp., Arcoppia aff. dechambrierorum and Suctobelbella sp. presented as dominant (D),
very abundant (ma), very frequent (MF) and constant (W) in the end of rainy period (Table 1). In most soils, oribatid mites are
numerically dominat and the most diverse among microarthropods, especially among soil invertebrates [25].
TABLE 1
FAUNISTIC ANALYSIS FOR TAXA OF EDAPHIC MITES COLLECTED BETWEEN THE LINES OF THE COFFEE
PLANTATION AND FOREST AT THE END OF THE RAINY SEASON OF 2013. SÃO SEBASTIÃO DO PARAÍSO, MG.
Taxa (Suborder, cohort, family, genus and species)
Number of Number of samples in which
specimens
was recorded (n = 48)
D1
A2
F3
C4
Galumna flabellifera (Oribatida, Galumnidae)
138
4
D
ma
MF
W
Rizoglyphus sp. (Astigmatina, Acaridae) (Hypopus)
134
6
D
ma
MF
W
Scheloribates sp. (Oribatida, Scheloribatidae)
115
4
D
ma
MF
W
Oribatida, Licnodamaeidae
105
3
D
ma
MF
Y
Suctobelbella sp. (Oribatida, Suctobelbidae)
96
7
D
ma
MF
W
Eupodes sp.1 (Prostigmata, Eupodidae)
95
7
D
ma
MF
W
Arcoppia aff. dechambrierorum (Oribatida, Oppiidae)
81
5
D
ma
MF
W
Spelenorchestes sp. (Endeostigmata: Nanorchestidae)
78
5
D
ma
MF
W
Multidentorhodacarus sp.1 (Mesostigmata, Rhodacaridae)
67
6
D
ma
F
W
Oribatida, Brachichthoniidae
Tarsonemus sp. (Prostigmata, Heterostigmatina,
Tarsonemidae)
Oribatida (immature) (sp.9) (Suborder)
54
6
D
ma
MF
W
48
6
D
ma
MF
W
46
5
D
ma
MF
W
Multidentorhodacarus sp.2 (Mesostigmata, Rhodacaridae)
39
5
D
ma
MF
W
Eremulus crispus (Oribatida, Eremulidae)
38
3
D
ma
MF
Y
Bimichaelia sp. (Endeostigmata, Alycidae)
37
5
D
ma
MF
W
Oribatida (immature) (sp.23) (Suborder)
37
8
D
ma
MF
W
Berlezetes brasilozetoides (Oribatida, Microzetidae)
36
6
D
ma
MF
W
Eupodes sp.2 (Prostigmata, Eupodidae)
32
5
D
ma
MF
W
Microdispidae (Prostigmata, Heterostigmata)
27
4
D
a
MF
W
Oplitis sp. (Mesostigmata, Uropodina, Oplitidae)
Epilohmannia pallida americana (Oribatida,
Epilohmanniidae)
Oribatida (immature) (sp.47) (Suborder)
25
3
D
c
F
W
25
6
D
c
F
W
24
5
D
c
F
W
Prostigmata, Heterostigmata, Pygmephoridae
20
3
D
c
F
Y
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International Journal of Environmental & Agriculture Research (IJOEAR)
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
Protogamasellus mica (Mesostigmata, Ascidae)
18
5
D
c
F
W
Cultroribula zicsii (Oribatida, Astegistidae)
18
2
D
c
F
Y
Protogamasellus sigillophorus (Mesostigmata, Ascidae)
17
4
D
c
F
W
Asca sp.1 (Mesostigmata, Ascidae)
16
3
D
c
F
W
Lamellobates molecula (Oribatida, Austrachipteriidae)
16
2
D
c
F
Y
Oribatida, Phthiracaridae
16
4
D
c
F
W
Rhizoglyphus sp. (Astigmatina, Acaridae)
15
4
D
c
F
W
Ramusella (Insculptoppia) sp. (Oribatida, Oppiidae)
14
1
D
c
F
Z
Scutacarus sp. (Prostigmata, Heterostigmata, Scutacaridae)
14
3
D
c
F
Y
Mesostigmata, Gamasina, Uropodina (sp.2) (Cohort)
13
4
D
c
F
W
Continua…
Continuação
Number of
specimens
Number of samples in which
was recorded (n = 48)
D1
A2
F3
C4
Prostigmata, Bdelloidea, Cunaxidae (sp.1)
13
5
D
c
F
W
Mesostigmata, Gamasina, Ologamasidae, (sp.2)
12
3
D
d
PF
W
Rhodacarellus sp. (Mesostigmata, Rhodacaridae)
Torpacarus ommitens paraguayensis (Oribatida,
Lohmanniidae)
Mesostigmata, Gamasina, Uropodina (sp.4) (Cohort)
12
4
D
d
PF
W
12
1
D
d
PF
Z
11
3
D
d
PF
Y
Oribatida (immature) (sp.25) (Suborder)
11
3
D
d
PF
Y
Mesostigmata, Gamasina, Ologamasidae (sp.1)
9
1
D
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.3) (Cohort)
9
1
D
r
PF
Z
Striatoppia sp. (Oribatida, Oppiidae)
9
4
D
r
PF
W
Nanorchestes sp. (Endeostigmata, Nanorchestidae)
8
4
D
r
PF
W
Eohypochthonius sp. (Oribatida, Hypochthoniidae)
8
1
D
r
PF
Z
Oribatida (immature) (sp.3) (Suborder)
8
8
D
r
PF
W
Oribatida (immature) (sp.14) (Suborder)
8
3
D
r
PF
W
Pseudoparasitus sp. (Mesostigmata, Laelapidae)
6
1
D
r
PF
Z
Prostigmata, Heterostigmata, Scutacaridae (sp.1)
5
3
ND
r
PF
Y
Gaeolaelaps sp.1 (Mesostigmata, Laelapidae)
4
2
ND
r
PF
W
Eremobelba zicsii (Oribatida, Eremobelbidae)
4
1
ND
r
PF
Z
Oppiella nova (Oribatida, Oppiidae)
4
1
ND
r
PF
Z
Tectocepheus velatus (Oribatida, Tectocepheidae)
4
2
ND
r
PF
Y
Stigmaeus sp. (Prostigmata, Eleutherengona, Stigmaeidae)
4
2
ND
r
PF
Y
Prostigmata, Tydeidae
4
2
ND
r
PF
Y
Alycus sp. (Endeostigmata, Alycidae)
3
1
ND
r
PF
Z
Proctolaelaps paulista (Mesostigmata, Ascidae)
3
2
ND
r
PF
W
Mesostigmata, Gamasina, Uropodina (sp.1) (Cohort)
3
1
ND
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.7) (Cohort)
3
2
ND
r
PF
Y
Oribatida (immature) (sp.29) (Suborder)
3
1
ND
r
PF
Z
Lohmanniidae, Oribatida
3
3
ND
r
PF
Y
Taxa (Suborder, cohort, family, genus and species)
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International Journal of Environmental & Agriculture Research (IJOEAR)
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[Vol-4, Issue-3, March- 2018]
Prostigmata, Tydeoidea, Ereynetidae
3
2
ND
r
PF
Y
Prostigmata, Eupodina, Rhagidiidae (sp.1)
3
2
ND
r
PF
Y
Mesostigmata, Gamasida, Eviphidae
Proprioseiopsis sp.2 (Mesostigmata, Gamasina,
Phytoseiidae)
Rhodacarus sp. (Mesostigmata, Rhodacaridae)
2
1
ND
r
PF
Z
2
1
ND
r
PF
Z
2
2
ND
r
PF
Y
Mesostigmata, Trachytidae
2
2
ND
r
PF
Y
Tyrophagus sp. (Astigmatina, Acaridae)
2
2
ND
r
PF
Y
Rysotritia peruensis (Oribatida, Euphthiracaridae)
2
1
ND
r
PF
Z
Continua…
Continuação
Number of
specimens
Number of samples in which
was recorded (n = 48)
D1
A2
F3
C4
Oribatida (immature) (sp.22) (Suborder)
2
1
ND
r
PF
Z
Oribatida (immature) (sp.8) (Suborder)
2
2
ND
r
PF
Y
Quadroppia circumita (Oribatida, Quadroppiidae)
2
1
ND
r
PF
Z
Bdella sp.1 (Prostigmata, Eupodina, Bdellidae)
2
1
ND
r
PF
Z
Prostigmata, Bdelloidea, Cunaxidae (sp.3)
2
1
ND
r
PF
Z
Rhagidia sp.2 (Prostigmata, Eupodina, Rhagidiidae)
2
1
ND
r
PF
Z
Rhaphignatus sp. (Prostigmata, Raphignathidae)
2
1
ND
r
PF
Z
Mesostigmata, Gamasina, Ameroseiidae
1
1
ND
r
PF
Z
Asca sp.2 (Mesostigmata, Ascidae)
1
1
ND
r
PF
Z
Protogamasellus sp.2 (Mesostigmata, Ascidae)
1
1
ND
r
PF
Z
Cosmolaelaps sp.1 (Mesostigmata, Laelapidae)
Typhlodromus sp.1 (Mesostigmata, Gamasina,
Phytoseiidae)
Podocinum sp. (Mesostigmata, Podocinidae)
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.9) (Cohort)
Adelphacarus sp. (Oribatida, Aphelacaridae,
Adelphacaridae syn.)
Fosseremus quadripertitus (Oribatida, Damaeolidae)
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
Brachioppia sp. (Oribatida, Oppiidae)
1
1
ND
r
PF
Z
Bdella sp.2 (Prostigmata, Eupodina, Bdellidae)
1
1
ND
r
PF
Z
Mexecheles sp. (Prostigmata, Eleutherengona, Cheyletidae)
1
1
ND
r
PF
Z
Cryptognathus sp. (Prostigmata, Cryptognathidae)
1
1
ND
r
PF
Z
Mesostigmata, Digamaselidae
1
1
ND
r
PF
Z
Prostigmata, Erythraeidae
1
1
ND
r
PF
Z
Prostigmata, Erythraeidae (sp.) (adult)
1
1
ND
r
PF
Z
Astigmatina, Pyemotidae
1
1
ND
r
PF
Z
Rhagidia sp.3 (Prostigmata, Eupodina, Rhagidiidae)
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
Taxa (Suborder, cohort, family, genus and species)
Prostigmata, Heterostigmata, Scutacaridae (sp2)
Total
1.788
1
Dominance: D - dominant, ND - non - dominant. Laroca and Meilke method [26], Moraes et al. [23].
2
Abundance: ma - very abundant, a - abundant, c - common, d - dispersed, r - rare.
3
Frequency: PF - little frequent, MF - very frequent, F - frequent.
4
Constancy: W - constant, Y - accessory, Z - accidental.
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International Journal of Environmental & Agriculture Research (IJOEAR)
3.2
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
Soil samples from the end of dry season
By the end of the dry season of 2013, the families Acaridae (Rhyzoglyphus sp.), Oplitidae (Oplitis sp.) and Eupodidae (Eupodes
sp.1), the suborder Oribatida, the cohort Uropodina (sp.2) and the hypopus phase (cohort Astigmatina, Family Acaridae, genus
Ryzopglyphus sp.) were the most favored. The oribatid were represented by 28 species and morphospecies and five families. The
oribatid Scherolibates spp., Galumna flabellifera, Arcoppia aff. dechambrierorum, Epilohmannia pallida americana, Eremulus
crispus, Berlezetes brasilozetoides, Suctobelbella sp. and the family Licnodomaeidae were the most representative, being
dominant (D), very abundant (ma), very frequent (MF) and constant (W) during the evaluation of the end of dry season (Table 2).
TABLE 2
FAUNISTIC ANALYSIS FOR TAXA OF EDAPHIC MITES COLLECTED BETWEEN THE LINES OF THE COFFEE
PLANTATION AND FOREST AT THE END OF THE DRY SEASON OF 2013. SÃO SEBASTIÃO DO PARAÍSO, MG.
Taxa (Suborder, cohort, family, genus and species)
Number of
specimens
Number of samples in which
D1
was recorded (n = 48)
A2
F3
C4
Rizoglyphus sp. (Astigmatina, Acaridae) (Hypopus)
492
17
D
ma MF
W
Scheloribates sp. (Oribatida, Scheloribatidae)
164
7
D
ma MF
W
Suctobelbella sp. (Oribatida, Suctobelbidae)
154
7
D
ma MF
W
Oplitis sp. (Mesostigmata, Uropodina, Oplitidae)
153
16
D
ma MF
W
Galumna flabellifera (Oribatida, Galumnidae)
133
7
D
ma MF
W
Oribatida, Licnodamaeidae
118
7
D
ma MF
W
Rizoglyphus sp. (Astigmatina, Acaridae)
91
6
D
ma MF
W
Eupodes sp.1 (Prostigmata, Eupodidae)
73
7
D
ma MF
W
Arcoppia aff. dechambrierorum (Oribatida, Oppiidae)
60
7
D
ma MF
W
Epilohmannia pallida americana (Oribatida, Epilohmanniidae)
52
8
D
ma MF
W
Eremulus crispus (Oribatida, Eremulidae)
40
6
D
ma MF
W
Berlezetes brasilozetoides (Oribatida, Microzetidae)
34
6
D
ma MF
W
Mesostigmata, Gamasina, Uropodina (sp.2) (Cohort)
32
4
D
ma MF
W
Prostigmata, Heterostigmata, Pygmephoridae
27
2
D
c
F
Y
Cultroribula zicsii (Oribatida, Astegistidae)
25
5
D
c
F
W
Spelenorchestes sp. (Endeostigmata: Nanorchestidae)
22
6
D
c
F
W
Protogamasellus mica (Mesostigmata, Ascidae)
20
5
D
c
F
W
Tarsonemus sp. (Prostigmata, Heterostigmatina, Tarsonemidae)
20
4
D
c
F
W
Oribatida (immature) sp.47 (Suborder)
19
5
D
c
F
W
Oribatida, Phthiracaridae
18
5
D
c
F
W
Protogamasellus sigillophorus (Mesostigmata, Ascidae)
16
3
D
c
F
Y
Oribatida (immature) (sp. 9) (Suborder)
16
7
D
c
F
W
Ramusella (Insculptoppia) sp. (Oribatida, Oppiidae)
16
4
D
c
F
W
Multidentorhodacarus sp.1 (Mesostigmata, Rhodacaridae)
15
5
D
c
F
W
Mesostigmata, Gamasina, Uropodina (sp.3) (Cohort)
15
4
D
c
F
W
Prostigmata, Bdelloidea, Cunaxidae (sp.1)
15
6
D
c
F
W
Gaeolaelaps sp.1 (Mesostigmata, Laelapidae)
13
4
D
c
F
W
Proctolaelaps paulista (Mesostigmata, Ascidae)
13
4
D
c
F
W
Mesostigmata, Gamasina, Uropodina (sp.4) (Cohort)
13
3
D
c
F
W
Mesostigmata, Gamasina, Uropodina (sp.5) (Cohort)
13
4
D
c
F
W
Oribatida (immature) (sp. 23) (Suborder)
13
6
D
c
F
W
Continua…
Page | 48
International Journal of Environmental & Agriculture Research (IJOEAR)
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
Continuação
Taxa (Suborder, cohort, family, genus and species)
Number of
specimens
Number of samples in which
D1
was recorded (n = 48)
A2
F3
C4
Mesostigmata, Gamasina, Ologamasidae (sp.1)
12
4
D
c
F
W
Rostrozetes foveolatus (Oribatida, Haplozetidae )
12
2
D
c
F
Y
Tectocepheus velatus (Oribatida, Tectocepheidae)
12
3
D
c
F
Y
Winterschmidtiidae, Astigmata
12
2
D
c
F
Y
Striatoppia sp. (Oribatida, Oppiidae)
11
5
D
c
F
W
Bimichaelia sp. (Endeostigmata, Alycidae)
9
4
D
c
F
W
Multidentorhodacarus sp.2 (Mesostigmata, Rhodacaridae)
9
2
D
c
F
Y
Oribatida (immature) (sp.25) (Suborder)
9
4
D
c
F
W
Nothrus aff. monticola (Oribatida, Nothridae)
9
1
D
c
F
Z
Xylobates capucinus (Oribatida, Haplozetidae)
9
2
D
c
F
W
Mesostigmata, Gamasina, Uropodina (sp.1) (Cohort)
8
4
D
d
PF
W
Nanorchestes sp. (Endeostigmata, Nanorchestidae)
7
4
D
d
PF
W
Rhodacarellus sp. (Mesostigmata, Rhodacaridae)
7
2
D
d
PF
Y
Lamellobates molecula (Oribatida, Austrachipteriidae)
7
4
D
d
PF
W
Oribatida, Brachichthoniidae
7
3
D
d
PF
W
Malacoangelia sp. (Oribatida, Hypochthoniidae)
7
1
D
d
PF
Z
Graptoppia sp. (Oribatida, Oppiidae)
7
1
D
d
PF
Z
Neosuctobelba transitoria (Oribatida, Suctobelbidae)
7
3
D
d
PF
W
Cosmolaelaps sp.3 (Mesostigmata, Laelapidae)
6
2
D
r
PF
Y
Mesostigmata, Laelapidae (sp.1)
6
2
D
r
PF
Y
Prostigmata, Heterostigmatina, Scutacaridae (sp.1)
6
4
D
r
PF
W
Gaeolaelaps sp.2 (Mesostigmata, Laelapidae)
5
2
ND
r
PF
Y
Hypoaspis sp.1 (Mesostigmata, Laelapidae)
5
2
ND
r
PF
Y
Mesostigmata, Gamasina, Uropodina, Trachytidae
5
2
ND
r
PF
Y
Tyrophagus sp. (Astigmatina, Acaridae)
5
4
ND
r
PF
W
Eremobelba zicsii (Oribatida, Eremobelbidae)
5
2
ND
r
PF
Y
Acrotritia (Rysotritia) peruensis (Oribatida, Euphthiracaridae)
5
2
ND
r
PF
Y
Oribatida (immature) (sp.14) (Suborder)
5
5
ND
r
PF
W
Microppia minus (Oribatida, Oppiidae)
5
1
ND
r
PF
Z
Mesostigmata, Dermanyssina, Digamasellidae
5
4
ND
r
PF
W
Asca sp.1 (Mesostigmata, Ascidae)
4
3
ND
r
PF
Y
Mesostigmata, Gamasina, Ologamasidae (sp.2)
4
3
ND
r
PF
Y
Proprioseiopsis sp.2 (Mesostigmata, Gamasina, Phytoseiidae)
4
2
ND
r
PF
Y
Rhodacarus sp. (Mesostigmata, Rhodacaridae)
Pseudoamerioppia barrancensis paraguayensis (Oribatida,
Oppiidae)
4
2
ND
r
PF
Y
4
3
ND
r
PF
Y
Continua…
Continuação
Page | 49
International Journal of Environmental & Agriculture Research (IJOEAR)
Taxa (Suborder, cohort, family, genus and species)
ISSN:[2454-1850]
Number of
specimens
[Vol-4, Issue-3, March- 2018]
Number of samples in which
D1
was recorded (n = 48)
A2
F3
C4
Rhagidia sp.1(Prostigmata, Eupodina, Rhagidiidae)
4
2
ND
r
PF
Y
Mesostigmata, Gamasina, Eviphidae
3
3
ND
r
PF
Y
Mesostigmata, Gamasina, Uropodina (sp.6) (Cohort)
3
3
ND
r
PF
Y
Astigmatina (Cohort)
3
1
ND
r
PF
Z
Eohypochthonius sp. (Oribatida, Hypochthoniidae )
3
1
ND
r
PF
Z
Tegeozetes sp. (Oribatida, Tectocepheidae)
3
1
ND
r
PF
Z
Prostigmata, Erythraeidae
3
2
ND
r
PF
Y
Protigmata, Heterostigmata, Microdispidae
3
2
ND
r
PF
Y
Prostigmata, Eupodina, Rhagidiidae (sp.1)
3
3
ND
r
PF
Y
Prostigmata, Heterostigmata, Scutacaridae (sp.2)
3
2
ND
r
PF
Y
Stigmaeus sp. (Prostigmata, Eleutherengona, Stigmaeidae)
3
3
ND
r
PF
Y
Asca sp.2 (Mesostigmata, Ascidae)
2
2
ND
r
PF
Y
Asca sp.3 (Mesostigmata, Ascidae)
2
2
ND
r
PF
Y
Cosmolaelaps sp.1 (Mesostigmata, Laelapidae)
2
2
ND
r
PF
Y
Gaeolaelaps sp.3 (Mesostigmata, Laelapidae)
2
1
ND
r
PF
Z
Hypoaspis sp.3 (Mesostigmata, Laelapidae)
2
1
ND
r
PF
Z
Chelaseius sp. (Mesostigmata, Phytoseiidae)
2
1
ND
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.10) (Cohort)
2
1
ND
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.7) (Cohort)
2
2
ND
r
PF
Y
Mesostigmata, Gamasina, Uropodina (sp.9) (Cohort)
2
1
ND
r
PF
W
Fosseremus quadripertitus (Oribatida, Damaeolidae)
2
1
ND
r
PF
Z
Oribatida (immature) (sp.22) (Suborder)
2
1
ND
r
PF
Z
Oribatida (immature) (sp.29) (Suborder)
2
1
ND
r
PF
Z
Oppiella nova (Oribatida, Oppiidae)
2
1
ND
r
PF
Z
Prostigma, Anystina, Anystidae
2
2
ND
r
PF
Y
Ctenacarus sp. (Oribatida, Ctenacaridae)
2
1
ND
r
PF
Z
Rhagidia sp.3 (Prostigmata, Eupodina, Rhagidiidae)
2
1
ND
r
PF
Z
Scutacarus sp. (Prostigmata, Heterostigmata, Scutacaridae)
2
2
ND
r
PF
Y
Prostigmata, Eleutherengona, Stigmaeidae (sp.1)
2
2
ND
r
PF
Y
Alycus sp. (Endeostigmata, Alycidae)
1
1
ND
r
PF
Z
Mesostigmata, Gamasina, Ameroseiidae
1
1
ND
r
PF
Z
Cosmolaelaps sp.2 (Mesostigmata, Laelapidae)
1
1
ND
r
PF
Z
Stratiolaelaps sp. (Mesostigmata, Laelapidae)
1
1
ND
r
PF
Z
Mesostigmata, Gamasina, Macrochelidae (sp 1)
1
1
ND
r
PF
Z
Pseudoparasitus sp. (Mesostigmata, Laelapidae)
1
1
ND
r
PF
Z
Continua…
Continuação
Page | 50
International Journal of Environmental & Agriculture Research (IJOEAR)
Taxa (Suborder, cohort, family, genus and species)
ISSN:[2454-1850]
Number of
specimens
[Vol-4, Issue-3, March- 2018]
Number of samples in which
D1
was recorded (n = 48)
A2
F3
C4
Neoseiulus sp. (Gamasina, Mesostigmata)
1
1
ND
r
PF
Z
Proprioseiopsis sp.3 (Mesostigmata, Gamasina, Phytoseiidae)
1
1
ND
r
PF
Z
Proprioseiopsis sp.4 (Mesostigmata, Gamasina, Phytoseiidae)
1
1
ND
r
PF
Z
Typhlodromus sp.2 (Mesostigmata, Gamasina, Phytoseiidae)
1
1
ND
r
PF
Z
Podocinum sp. (Mesostigmata, Podocinidae)
Protogamasellopsis sp. (Mesostigmata, Gamasina,
Rhodacaridae)
Astigmatina, Histiostomatidae
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
Oribatida (immature) (sp.3) (Suborder)
1
1
ND
r
PF
Z
Oribatida, Lohmanniidae
1
1
ND
r
PF
Z
Papillacarus sp. (Oribatida, Lohmanniidae)
1
1
ND
r
PF
Z
Oribatida, Oppiidae (sp.)
1
1
ND
r
PF
Z
Brasilobates bipilis (Oribatida, Xylobatidae)
1
1
ND
r
PF
Z
Quadroppia circumita (Oribatida, Quadroppiidae)
1
1
ND
r
PF
Z
Zetorchestes schusteri (Oribatida, Zetorchestidae)
1
1
ND
r
PF
Z
Prostigmata, Caligonellidae
1
1
ND
r
PF
Z
Mexecheles sp. (Prostigmata, Eleutherengona, Cheyletidae)
1
1
ND
r
PF
Z
Prostigmata, Bdelloidea, Cunaxidae (sp.5)
1
1
ND
r
PF
Z
Prostigmata, Tydeoidea, Ereynetidae
1
1
ND
r
PF
Z
Eupodes sp.2 (Prostigmata, Eupodidae)
1
1
ND
r
PF
Z
Rhagidia sp.2 (Prostigmata, Eupodina, Rhagidiidae)
1
1
ND
r
PF
Z
Prostigmata, Eupodina, Rhagidiidae (sp.2)
1
1
ND
r
PF
Z
Prostigmata, Eleutherengona, Stigmaeidae (sp.2)
1
1
ND
r
PF
Z
Total
2.247
1
Dominance: D - dominant, ND - non - dominant. Laroca and Meilke method [26], Moraes et al. [23].
2
Abundance: ma - very abundant, a - abundant, c - common, d - dispersed, r - rare.
3
Frequency: PF - little frequent, MF - very frequent, F - frequent.
4
Constancy: W - constant, Y - accessory, Z - accidental.
3.3
Soil samples from the end of rainy season plus end of dry season
In the analysis performed on the total of mites found at the end of the rainy season plus those found at the end of the dry period of
2013, the families Nanorchestidae (Spelenorchestes sp.), Oplitidae (Oplitis sp.), Acaridae (Rhyzoglyphus sp.), Alycidae
(Bimichaelia sp.), cohort Astigmatina (in the hypopus phase), Eupodidae (Eupodes sp.1), Rhodacaridae (Multidentorhodacarus
sp.1), Pygmephoridae, Tarsonemidae (Tarsonemus sp.), the cohort Uropodina (sp.2) and the suborder Oribatida, presented the
maximum rates of faunistic classification, dominant (D), very abundant (ma), very frequent (MF) and constant (W), that is, in the
sum of the two samples made (Table 3).
Regarding the dominance, it was verified that of the total of 139 Suborder, cohort, family, genus, species collected, 71 were
considered dominant (D). Dominant species have the capacity to modify an impact received from the environment for their own
benefit, which may lead to the appearance or disappearance of other species [24].
Regarding the classification of abundance, 105 species, subspecies and families were categorized as rare (r). However, even
though they are rare, they are important because they have a high influence on the diversity of ecosystems. The substitutions of
species and arrangements in the abundance are part of the development of the ecosystem in search of the equilibrium [27].
Page | 51
International Journal of Environmental & Agriculture Research (IJOEAR)
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
In the classification of constancy, 90 species, subspecies and families were accidental (Z). Many species presented small numbers
of specimens, and these specimens did not present constancy in the samples. The large number of accidental species associated to
the high diversity index, show a balanced environment where interspecific and intraspecific competitions can determine species
behavior [28].
TABLE 3
FAUNISTIC ANALYSIS FOR TAXA OF EDAPHIC MITES COLLECTED BETWEEN THE LINES OF THE COFFEE
PLANTATION AND FOREST AT THE END OF THE DRY SEASON PLUS THOSE FOUND AT THE END OF THE RAINY
SEASON OF 2013. SÃO SEBASTIÃO DO PARAÍSO, MG.
Number of
specimens
Number of samples in which
was recorded (n = 48)
D1
A2
F3
C4
Rizoglyphus sp. (Astigmatina, Acaridae) (Hypopus)
626
23
D
ma MF
W
Scheloribates sp. (Oribatida, Scheloribatidae)
279
11
D
ma MF
W
Galumna flabellifera (Oribatida, Galumnidae)
271
11
D
ma MF
W
Suctobelbella sp. (Oribatida, Suctobelbidae)
250
14
D
ma MF
W
Oribatida, Licnodamaeidae
223
10
D
ma MF
W
Oplitis sp. (Mesostigmata, Uropodina, Oplitidae)
178
19
D
ma MF
W
Eupodes sp.1 (Prostigmata, Eupodidae)
168
14
D
ma MF
W
Arcoppia aff. dechambrierorum (Oribatida, Oppiidae)
141
12
D
ma MF
W
Rhizoglyphus sp. (Astigmatina, Acaridae)
106
10
D
ma MF
W
Spelenorchestes sp. (Endeostigmata: Nanorchestidae)
100
11
D
ma MF
W
Multidentorhodacarus sp.1(Mesostigmata, Rhodacaridae)
82
11
D
ma MF
W
Eremulus crispus (Oribatida, Eremulidae)
Epilohmannia pallida americana (Oribatida,
Epilohmanniidae)
Berlezetes brasilozetoides (Oribatida, Microzetidae)
Tarsonemus sp. (Prostigmata, Heterostigmata,
Tarsonemidae)
Oribatida (immature) (sp.9) (Suborder)
78
9
D
ma MF
W
77
14
D
ma MF
W
70
12
D
ma MF
W
68
10
D
ma MF
W
62
12
D
ma MF
W
Oribatida, Brachichthoniidae
61
9
D
ma MF
W
Oribatida (immature) (sp.23) (Suborder)
50
14
D
ma MF
W
Multidentorhodacarus sp.2 (Mesostigmata, Rhodacaridae)
48
7
D
ma MF
Y
Prostigmata, Heterostigmata, Pygmephoridae
47
5
D
ma MF
Y
Bimichaelia sp. (Endeostigmata, Alycidae)
46
9
D
ma MF
W
Mesostigmata, Gamasina, Uropodina (sp.2) (Cohort)
45
8
D
ma MF
W
Taxa (Suborder, cohort, family, genus and species)
Continua…
Continuação
Number of
specimens
Number of samples in which
was recorded (n = 48)
D1
A2
F3
C4
Cultroribula zicsii (Oribatida, Astegistidae)
43
7
D
a
MF
Y
Oribatida (immature) (sp.47) (Suborder)
43
10
D
a
MF
W
Protogamasellus mica (Mesostigmata, Ascidae)
38
10
D
c
F
W
Oribatida, Phthiracaridae
34
9
D
c
F
W
Taxa (Suborder, cohort, family, genus and species)
Page | 52
International Journal of Environmental & Agriculture Research (IJOEAR)
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
Protogamasellus sigillophorus (Mesostigmata, Ascidae)
33
7
D
c
F
Y
Eupodes sp.2 (Prostigmata, Eupodidae)
33
6
D
c
F
Y
Ramusella (Inculptoppia) sp. (Oribatida, Oppiidae)
30
5
D
c
F
Y
Prostigmata, Heterostigmata, Microdispidae
30
6
D
c
F
Y
Prostigmata, Bdelloidea, Cunaxidae (sp.1)
28
11
D
c
F
W
Mesostigmata, Gamasina, Uropodina (sp.3) (Cohort)
24
5
D
c
F
Y
Mesostigmata, Gamasina, Uropodina (sp.4) (Cohort)
24
6
D
c
F
Y
Lamellobates molecula (Oribatida, Austrachipteriidae)
23
6
D
c
F
Y
Mesostigmata, Gamasina, Ologamasidae (sp.1)
21
5
D
c
F
Y
Asca sp.1 (Mesostigmata, Ascidae)
20
6
D
c
F
Y
Oribatida (immature) (sp.25) (Suborder)
20
7
D
c
F
Y
Striatoppia sp. (Oribatida, Oppiidae)
Rhodacarellus sp. (Mesostigmata, Gamasina,
Rhodacaridae)
Proctolaelaps paulista (Mesostigmata, Ascidae)
20
9
D
c
F
W
19
6
D
c
F
Y
16
6
D
d
PF
Y
Mesostigmata, Gamasina, Ologamasidae (sp.2)
16
6
D
d
PF
Y
Tectocepheus velatus (Oribatida, Tectocepheidae)
16
5
D
d
PF
Y
Scutacarus sp. (Prostigmata, Heterostigmata, Scutacaridae)
16
5
D
d
PF
Y
Nanorchestes sp. (Endeostigmata, Nanorchestidae)
15
8
D
d
PF
W
Gaeolaelaps sp.1 (Mesostigmata, Laelapidae)
13
4
D
r
PF
Y
Mesostigmata, Gamasina, Uropodina (sp.5) (Cohort)
13
4
D
r
PF
Y
Oribatida (immature) (sp.14) (Suborder)
13
8
D
r
PF
W
Rostrozetes faveolatus (Oribatida, Haplozetidae)
Torpacarus ommitens paraguayensis (Oribatida,
Lohmanniidae)
Winterschmidtiidae, Astigmata
12
2
D
r
PF
Z
12
1
D
r
PF
Z
12
2
D
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.1) (Cohort)
11
5
D
r
PF
Y
Prostigmata, Heterostigmata, Scutacaridae (sp.1)
11
7
D
r
PF
Y
Eremobelba zicsii (Oribatida, Eremobelbidae)
9
3
D
r
PF
Z
Oribatida (immature) (sp.3) (Suborder)
9
9
D
r
PF
W
Xylobates capucinus (Oribatida, Haplozetidae)
9
2
D
r
PF
Z
Nothrus aff. monticola (Oribatida, Nothridae)
9
1
D
r
PF
Z
Eohypochthonius sp. (Oribatida, Hypochthoniidae)
8
1
D
r
PF
Z
Continua…
Continuação
Number of
specimens
Number of samples in which
was recorded (n = 48)
D1
A2
F3
C4
Pseudoparasitus sp. (Mesostigmata, Laelapidae)
7
2
D
r
PF
Z
Mesostigmata, Gamasina, Uropodina, Trachytidae
7
4
D
r
PF
Y
Tyrophagus sp. (Astigmatina, Acaridae)
7
6
D
r
PF
Y
Rysotritia peruensis (Oribatida, Euphthiracaridae)
7
3
D
r
PF
Z
Malacoangelia sp. (Oribatida, Hypochthoniidae)
7
1
D
r
PF
Z
Taxa (Suborder, cohort, family, genus and species)
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International Journal of Environmental & Agriculture Research (IJOEAR)
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[Vol-4, Issue-3, March- 2018]
Neosuctobelba transitoria (Oribatida, Suctobelbidae)
7
3
D
r
PF
Z
Graptoppia sp. (Oribatida, Oppiidae)
7
1
D
r
PF
Z
Stigmaeus sp. (Prostigmata, Eleutherengona, Stigmaeidae)
7
5
D
r
PF
Y
Cosmolaelaps sp.3 (Mesostigmata, Laelapidae)
6
2
D
r
PF
Z
Mesostigmata, Laelapidae (sp.1)
Proprioseiopsis sp.2(Mesostigmata, Gamasina,
Phytoseiidae)
Rhodacarus sp. (Mesostigmata, Rhodacaridae)
6
2
D
r
PF
Z
6
3
D
r
PF
Z
6
4
D
r
PF
Y
Oppiella nova (Oribatida, Oppiidae)
6
2
D
r
PF
Z
Prostigmata, Eupodina, Rhagidiidae (sp.1)
6
5
D
r
PF
Y
Mesostigmata, Gamasina, Eviphidae
5
4
ND
r
PF
Y
Cosmolaelaps sp.2 (Mesostigmata, Laelapidae)
5
3
ND
r
PF
Z
Gaeolaelaps sp.2 (Mesostigmata, Laelapidae)
5
2
ND
r
PF
Z
Hypoaspis sp.1 (Mesostigmata, Laelapidae)
5
2
ND
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.7) (Cohort)
5
4
ND
r
PF
Y
Oribatida (immature) (sp.29) (Suborder)
5
2
ND
r
PF
Z
Microppia minus (Oribatida, Oppiidae)
5
1
ND
r
PF
Z
Prostigmata, Bdelloidea, Cunaxidae (sp.5)
5
4
ND
r
PF
Y
Alycus sp. (Endeostigmata, Alycidae)
4
2
ND
r
PF
Z
Oribatida (immature) (sp. 22) (Suborder)
4
2
ND
r
PF
Z
Oribatida, Lohmanniidae
Pseudoamerioppia barrancensis paraguayensis (Oribatida,
Oppiidae)
Prostigmata, Tydeoidea, Ereynetidae
4
4
ND
r
PF
Y
4
3
ND
r
PF
Z
4
3
ND
r
PF
Z
Prostigmata, Erythraeidae
4
3
ND
r
PF
Z
Rhagidia sp.1(Prostigmata, Eupodina, Rhagidiidae)
4
2
ND
r
PF
Z
Prostigmata, Heterostigmata, Scutacaridae (sp.2)
4
3
ND
r
PF
Z
Prostigmata, Tydeidae
4
N
ND
r
PF
Z
Asca sp.2 (Mesostigmata, Ascidae)
3
3
ND
r
PF
Z
Cosmolaelaps sp.1 (Mesostigmata, Laelapidae)
3
3
ND
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.6) (Cohort)
3
3
ND
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.9) (Cohort)
3
2
ND
r
PF
Z
Continua…
Continuação
Number of
specimens
Number of samples in which
was recorded (n = 48)
D1
A2
F3
C4
Fosseremus quadripertitus (Oribatida, Damaeolidae)
3
2
ND
r
PF
Z
Eohypochthonius sp. (Oribatida, Hypochthoniidae)
3
1
ND
r
PF
Z
Astigmatina (Cohort)
3
1
ND
r
PF
Z
Quadroppia circumita (Oribatida, Quadroppiidae)
3
2
ND
r
PF
Z
Tegeozetes sp. (Oribatida, Tectocepheidae)
3
1
ND
r
PF
Z
Rhagidia sp.2 (Prostigmata, Eupodina, Rhagidiidae)
3
2
ND
r
PF
Z
Taxa (Suborder, cohort, family, genus and species)
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International Journal of Environmental & Agriculture Research (IJOEAR)
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[Vol-4, Issue-3, March- 2018]
Rhagidia sp.3(Prostigmata, Eupodina, Rhagidiidae)
3
3
ND
r
PF
Z
Mesostigmata, Gamasina, Ameroseiidae
2
2
ND
r
PF
Z
Asca sp.3 (Mesostigmata, Ascidae)
2
2
ND
r
PF
Z
Gaeolaelaps sp.3 (Mesostigmata, Laelapidae)
2
1
ND
r
PF
Z
Hypoaspis sp.3 (Mesostigmata, Laelapidae)
2
1
ND
r
PF
Z
Chelaseius sp. (Mesostigmata, Phytoseiidae)
2
2
ND
r
PF
Z
Podocinum sp. (Mesostigmata, Podocinidae)
2
2
ND
r
PF
Z
Mesostigmata, Gamasina, Uropodina (sp.10) (Cohort)
2
1
ND
r
PF
Z
Oribatida (immature) (sp.8) (Suborder)
2
2
ND
r
PF
Z
Bdella (sp.1) (Prostigmata, Eupodina, Bdellidae)
2
1
ND
r
PF
Z
Prostigmata, Bdelloidea, Cunaxidae (sp.3)
2
1
ND
r
PF
Z
Rhaphignatus sp. (Prostigmata, Raphignathidae)
2
1
ND
r
PF
Z
Prostigma, Anystina, Anystidae
2
2
ND
r
PF
Z
Ctenacarus sp. (Oribatida, Ctenacaridae)
2
1
ND
r
PF
Z
Prostigmata, Eleutherengona, Stigmaeidae (sp.1)
2
2
ND
r
PF
Z
Protogamasellus sp.2 (Mesostigmata, Ascidae)
1
1
ND
r
PF
Z
Stratiolaelaps sp. (Mesostigmata, Laelapidae)
1
1
ND
r
PF
Z
Mesostigmata, Gamasina, Macrochelidae (sp1)
Proprioseiopsis sp.3 (Mesostigmata, Gamasina,
Phytoseiidae)
Proprioseiopsis sp.4 (Mesostigmata, Gamasina,
Phytoseiidae)
Typhlodromus sp.1 (Mesostigmata, Gamasina,
Phytoseiidae)
Typhlodromus sp.2 (Mesostigmata, Gamasina,
Phytoseiidae)
Neoseiulus sp. (Gamasina, Mesostigmata)
Protogamasellopsis sp. (Mesostigmata, Gamasina,
Rhodacaridae)
Adelphacarus sp. (Oribatida, Aphelacaridae,
Adelphacaridae syn.)
Astigmatina, Histiostomatidae
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
Brachioppia sp. (Oribatida, Oppiidae)
1
1
ND
r
PF
Z
Oribatida, Oppiidae (sp.)
1
1
ND
r
PF
Z
Brasilobates bipilis (Oribatida, Xylobatidae)
1
1
ND
r
PF
Z
Continua…
Continuação
Number of
specimens
Number of samples in which
was recorded (n = 48)
D1
A2
F3
C4
Papillacarus sp. (Oribatida, Lohmanniidae)
1
1
ND
r
PF
Z
Bdella (sp.2) (Prostigmata, Eupodina, Bdellidae)
1
1
ND
r
PF
Z
Mexecheles sp. (Prostigmata, Eleutherengona, Cheyletidae)
1
1
ND
r
PF
Z
Cryptognathus sp. (Prostigmata, Cryptognathidae)
1
1
ND
r
PF
Z
Taxa (Suborder, cohort, family, genus and species)
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International Journal of Environmental & Agriculture Research (IJOEAR)
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[Vol-4, Issue-3, March- 2018]
Mesostigmata, Digamaselidae
1
1
ND
r
PF
Z
Prostigmata, Erythraeidae (sp.) (adulto)
1
1
ND
r
PF
Z
Astigmatina, Pyemotidae
1
1
ND
r
PF
Z
Prostigmata, Eupodina, Rhagidiidae (sp.2)
1
1
ND
r
PF
Z
Zetorchestes schusteri (Oribatida, Zetorchestidae)
1
1
ND
r
PF
Z
Prostigmata, Eleutherengona, Caligonellidae
1
1
ND
r
PF
Z
1
1
ND
r
PF
Z
Prostigmata, Eleutherengona, Stigmaeidae (sp.2)
Total
4.035
1
Dominance: D - dominant, ND - non - dominant. Laroca and Meilke method [26], Moraes et al. [23].
2
Abundance: ma - very abundant, a - abundant, c - common, d - dispersed, r - rare.
3
Frequency: PF - little frequent, MF - very frequent, F - frequent.
4
Constancy: W - constant, Y - accessory, Z - accidental.
Oribatid mites generally have little capacity in response short term environmental changes, i.e., their populations decline rapidly
when habitats are altered, a feature that may allow their use to detect environmental degradation [29] [30]. Changes in the
dominance structure of a soil microarthropods community may be a pre-indicator of environmental stress [31].
The decrease of oribatid mites number in the soil can compromise, in medium and long term, the processes of decomposition and
mineralization of organic matter, affecting the quality of the soil and, consequently, the entire ecological system. Mite debris
provides a large area for decomposition and, in turn, is an integral part of the soil structure, with direct or indirect effe cts on the
formation and maintenance of soil structure [29].
The species Oplitis sp. (Mesostigmata, Uropodina, Oplitidae) was found in all samples, however, this species was most
representative at the end of the dry season of 2013. The oribatid mites of the family Oppiidae, which in this work were found
both at the end of the dry season and at the end of the rainy season, are considered environmentally insensitive, and are
commonly found in disturbed habitats [32].
IV.
CONCLUSIONS
There is a difference in the abundance of soil mites when compared the end of the dry period with the end of the rainy season,
and the end of the dry period is generally more favorable to the edaphic mite community.
The cohort Astigmatina (family Acaridae) followed by the suborder Oribatida of mites, present the largest numbers of edaphic
species, both at the end of the dry period and at the end of the rainy season, and can be worked to be an indicative of the soil
quality.
ACKNOWLEDGEMENT
To Coordenação de Aperfeiçoamento de Pessoal de Nível Superior - Coordination of Improvement of Higher Level PersonnelCAPES, and Conselho Nacional de Desenvolvimento Científico e Tecnológico - National Council for Scientific and
Technological Development - CNPq and for granting scholarships.
To Dr. Pavel Klimov, University of Michigan, USA, for the identification of Acaridae family mites; Dr. Antônio Carlos Lofego,
from the State University of São Paulo, Campus of São José do Rio Preto, São Paulo, Brazil, for identification of the mites of the
Tarsonemidae family.
REFERENCES
[1]
[2]
Baretta, D.; Ferreira, C.S.; Sousa, J.P. and Cardoso, E.J.B.N. 2008. Colêmbolos (Hexapoda: Collembola) como bioindicadores de
qualidade do solo em áreas com Araucaria angustifolia. Revista Brasileira de Ciência do Solo, Viçosa, 32 (n.spe.):2.693-2.699.
http://dx.doi.org/10.1590/S0100-06832008000700012
Fialho, J.S.; Gomes, V.F.F.; Oliveira, T.S. and Silva Júnior, J.M.T. 2006. Indicadores da qualidade do solo em áreas sob vegetação
natural e cultivos de bananeira na Chapada do Apodi-CE. Revista Ciência Agronômica, Fortaleza, 37 (3):250-257.
Page | 56
International Journal of Environmental & Agriculture Research (IJOEAR)
[3]
[4]
[5]
[6]
[7]
[8]
[9]
[10]
[11]
[12]
[13]
[14]
[15]
[16]
[17]
[18]
[19]
[20]
[21]
[22]
[23]
[24]
[25]
[26]
[27]
[28]
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
Stork, N.E. and Eggleton, P. 1992. Invertebrates as determinants and indicators of soil quality. American Journal of Alternative
Agriculture, Greenbelt, 7, (1-2):38-47. https://doi.org/10.1017/S0889189300004446
Lavelle, P. 1996. Diversity of soil fauna and ecosystem function. Biology International, Oxford, 33:3-16.
http://citeseerx.ist.psu.edu/viewdoc/download?doi=10.1.1.491.2284&rep=rep1&type=pdf
Lavelle, P.; Blanchart, E.; Martin, A.; Spain, A.V. and Martin, S. 1992. Impact of soil fauna on the properties of soils in the humid
tropics. Paris, Ecole Normale Supkieure. 29p. (Special Publication, 29).
http://citeseerx.ist.psu.edu/viewdoc/download?doi=10.1.1.470.1874&rep=rep1&type=pdf
Swift, M.J.; Heal, O.W. and Anderson, J.M. 1979. Decomposition in terrestrial ecosystems. Berkeley, University of California Press.
372p.
Wardle, D.A. and Lavelle, P. 1997. Linkages between soil biota, plant litter quality and decomposition, p. 107-124. In: Cadisch, G. and
Giller, K.E., Eds., Driven by nature: plant litter quality and decomposition. Cambridge, CAB International. 409p.
Pereira, R.C.; Albanez, J.M. and Mamédio, I.M.P. 2012. Diversidade da meso e macrofauna edáfica em diferentes sistemas de manejo de
uso do solo em Cruz das Almas – BA. Magistra, Cruz das Almas, 24 (n.spe.):63-76.
Correia, M.E.F. 2002. Potencial de utilização dos atributos das comunidades de fauna e de grupos de invertebrados como bioindicadores
do manejo de ecossistemas. Seropédica, Embrapa Agrobiologia. 23 p. (Documentos, 175).
Assad, M.L.L. 1997. Fana do solo, p.363-444. In: Vagas, M.A.T. and Hungria, M., Eds., Biologia dos solos de cerrado. Planaltina,
Embrapa CPAC. 524p.
Sandler, R.; Falco, L.B.; Ciocco, C.; Luca, R. and Coviella, C.E. 2010. Eficiencia del embudo Berlese-Tullgren para extracción de
artrópodos edáficos em suelos arguidoles típicos de la província de Buenos Aires. Ciencia del Suelo, Buenos Aires, 28 (1):56-66.
Huber, A.C.L.K. and Morselli, T.B.G.A. 2011. Estudo da mesofauna (ácaros e colêmbolos) no processo da vermicompostagem. Revista
da FZVA, Uruguaiana, 18 (2):12-20.
Krantz, G.W. and Walter, D.E., Eds., 2009. A manual of acarology. 3rd ed. Lubbock, Texas Tech University Press. 807p.
Coleman, D.C. and Crossley Júnior, D.A. 1996. Fundamentals of soil ecology. San Diego, Academic Press. 205p.
Wallwork, J.A. 1970. Ecology of soil animals. England, McGraw-Hill. 283p.
Petersen, H. and Luxton, M. 1982. A comparative analysis of soil fauna populations and their role in decomposition processes. Oikos,
Copenhagen, 39 (3):287-388. 1982. http://www.jstor.org/stable/3544689
Paschoal, A.D.; Monteiro, A.R.; Ferraz, L.C.C.B. and Inomoto, M. M. 1996. Fundamentos de zoologia agrícola e parasitologia: animais
do meio rural e sua importância. Piracicaba, ESALQ - Departamento de Zoologia. 98p.
Oliveira, A.R. 1999. Efeito do Baculovirus anticarsia sobre Oribatida edáficos (Arachnida: Acari) na cultura da soja. 1999. 69 f.
Dissertação. (Mestrado em Zoologia) - Instituto de Biociências, Universidade de São Paulo, São Paulo, Brasil.
Mineiro, J.L.C. and Moraes, G.J. 2002. Actinedida e Acaridida (Arachnida: Acari) edáficos de Piracicaba, Estado de São Paulo.
Neotropical Entomology, Londrina, 31 (1):67-73. http://dx.doi.org/10.1590/S1519-566X2002000100010
Rieff, G.G.; Machado. R.G.; Stroschein, M.R.D. and Sá, E.L.S. 2010. Diversidade e famílias de ácaros e colêmbolos edáficos em cultivo
de eucalipto e áreas nativas. Current Agricultural Science and Technology formerly Revista Brasileira de Agrociências, Pelotas, 16 (14):57-61. http://periodicos.ufpel.edu.br/ojs2/index.php/CAST/
Pepato, A.R. and Klimov, P.B. 2015. Origin and higher-level diversification of acariform mites – evidence from nuclear ribosomal genes,
extensive taxon sampling, and secondary structure alignment. BMC Evolutionary Biology, 15 (178): 1-20.
https://doi.org/10.1186/s12862-015-0458-2
Oconnor, B.M. 2009. Cohort Astigmatina, p.565-657. In: Krantz, G.W. and; Walter, D.E., Eds., A manual of acarology. 3rd. ed. Lubbock,
Texas Tech University Press. 807p.
Moraes, R.C.B.; Haddad, M.L.; Silveira Neto, S. and Reyes, A.E.L. 2003. Software para análise faunística - ANAFAU. In: Simpósio
Nacional de Controle Biológico - SICOMBIOL, 8., 2003, São Pedro, São Paulo, Brasil. Anais... São Pedro, Sociedade Entomológica do
Brasil - ESALQ/USP. p.195.
Silveira Neto, S.; Nakano, O.; Barbin, D. and Villa Nova, N.A. 1976. Manual de ecologia dos insetos. São Paulo, Agronômica Ceres.
419p.
Norton, R.A. and Behan–Pelletier, V. 2009. Suborder Oribatida, p.430-564. In: Krantz, G.W. and Walter, D.E., Eds., A manual of
acarology. 3rd. ed. Lubbock, Texas Tech University Press. 807p.
Laroca, S. and Mielke, O.H.H. 1975. Ensaio sobre ecologia de comunidade em Sphingidae na Serra do Mar, Paraná, Brasil (Lepidoptera).
Revista Brasileira de Biologia, 35:1-19.
Souto, P.C. 2006. Acumulação e decomposição da serapilheira e distribuição de organismos edáficos em área de caatinga na Paraíba,
Brasil. 2006. 150f. Tese (Doutorado em Agronomia) - Universidade Federal da Paraíba, Paraíba, Areia, Brasil.
Bernardi, O.; Garcia, M.S.; Silva, E.J.E.; Zazycki, L.C.F.; Bernardi, D. and Finkenauer, E. 2011. Levantamento populacional e análise
faunística de Lepidoptera em Eucalyptus spp. no município de Pinheiro Machado, RS. Ciência Florestal, Santa Maria, 21 (4):735-744.
http://www.redalyc.org/articulo.oa?id=53421707012
Page | 57
International Journal of Environmental & Agriculture Research (IJOEAR)
ISSN:[2454-1850]
[Vol-4, Issue-3, March- 2018]
[29] Behan-Pelletier, V.M. 1999. Oribatid mite biodiversity in agroecossistems: role for bioindication. Agricultural, Ecossystem &
Environmental, Oxford, 74 (1-3):411-423. https://doi.org/10.1016/S0167-8809(99)00046-8
[30] Ducatti, F. 2002. Fauna edáfica em fragmentos florestais em áreas reflorestadas com espécie da mata atlântica. 2002. 70p. Dissertação
(Mestrado em Recursos Florestais) - Escola Superior de Agricultura Luiz de Queiroz, Universidade de São Paulo, São Paulo, Piracicaba,
Brasil.
[31] Hågvar, S. 1994. Log-normal distribution of dominance as an indicator of stressed soil microarthropod communities? Acta Zoologica
Fennica, 195:71-80.
[32] Aoki, J. 1979. Difference in sensitivities of oribatid families to environmental change by human impacts. European Journal of Soil
Biology formerly Revue D’Écologie et de Biologie du Sol, Paris, 16:415-422.
Page | 58