Evaluation of the Genotoxicity of Residual Repeated Applications of Sewage Sludge on M2 Meiocytes of Zea Plants
Amal W. Amin
The importance of the reuse of sewage sludge is derived from its high nutrient content that can improve the characteristics of the soil and kind of crop. Accordingly, it is important to characterize the genotoxicological potential of sewage sludge amended soil with such valuable properties "benefits". Field experiment was conducted to evaluate the residual effect of previous applications of sewage sludge used as biofertilizer on M2 meiocytes of Zea mays with different sludge rates (10, 20, 30 and 40 T/F for one and two additions). The resulting data demonstrated that M2 plants still have mutations in pollen mother cells. The total percentage of aberrant mother cells increased significantly with increasing sewage sludge concentration either by residual one or two additions. Aberrations was restricted to Metaphase one of Division one (DI) in the two groups of treatments, while, aberrant end product was the most frequent stage in Division two (DII). The most frequent kinds of aberrations were abnormal chromosome distribution and orientation, sticky figures, abnormal spindle behavior, overlapping cells, asynchronized cells and abnormal cell contour.
Received: January 22, 2011;
Accepted: July 22, 2011;
Published: October 31, 2011
Organic wastes are added to agricultural soils for increasing soil fertility
and plant nutrition. Plant and animal wastes as well as sewage sludge provided
by municipal sewage sludge refineries of urban wastes, has been added to agricultural
soils to increase its organic matter. Previous studies have demonstrated favorable
plant yield responses to the application of sewage sludge (Amin
et al., 2009a, b; Ashour
et al., 2007). In contrast, the effects of sewage sludge on soil
biological processes have been questioned by some authors (Solanoa
et al., 2009; Kizilkaya and Bayrakli, 2005;
Knight et al., 1997; Banerjee
et al., 1997). Knight et al. (1997)
observed a decrease of soil biological activity, such as microbial biomass and
enzyme activities, due to sewage sludge application. Conversely, Sastre
et al. (1996) and Banerjee et al. (1997)
found that sewage sludge amendment increased soil microbial activity and CO2
production. (Kizilkaya and Bayrakli, 2005) stated that
enzymatic activities in sludge-amended soils tended to decrease by increasing
incubation time. These differences might be a result of the difference in toxic
metal content of different sources of sewage sludge and/or its stability (Tam
and Wong, 1990). Heavy metals are significantly toxic, due to their cumulative
nature in different body organs leading to unwanted effects (Jarup,
2003; Sathawara et al., 2004). Metals tend
to reach toxic limits even when found in low concentrations. Monitoring programs
are being carried out in many countries to avoid the distribution of foodstuffs
that could pose a risk to human health if consumed. The chemical interactions
of toxic elements can interfere with proteins in living systems render essential
reactions important (Diamond and Zalups, 1998).
Applying treated municipal sewage sludge to agricultural soils to improve its
organic content has been used in Egypt for several decades. While plant nutrients
and organic matter are essential to plants, excessive application of nitrogen
and phosphorus was found to contaminate surface and groundwater or interfere
with good crop growth (Pivetz, 2001). Sludge also may
contain metals and some other constituents that can be harmful to humans if
accumulated applications are not managed properly. At the least, sludge application
can create a nuisance. Several communities regularly use sludge as biofertilizer
to benefit from municipal sewage. However, because of new regulations governing
the application of sludge to land, many questions are being asked by farmers,
utility managers, government officials and consultants about this alternative
(Singh and Agrawal, 2010). The Governments Regulation
for the application of sewage sludge should be applied in order to achieve the
following: pathogens disinfection, organic pollutants degradation, less available
heavy metals (as Cd, Pb, Ni, Co, Cr, Zn, Cu, Fe, Mn) and seed weeds destructions.
In addition, sewage sludge loading to agriculture land should be monitored as
excess application (El-Motaium and Abdel Monem, 2000;
Ghazy et al., 2009). Fuerhacker
and Haile (2011) pointed out the outcomes of different risk assessments.
Several studies using bean, maize and barley were stated dangerous levels of
some heavy metal(s) in the composted sewage sludge obtained from Alexandria
General Organization of Sanitary Drainage (AGOSD) of Alexandria (Amin,
2001; Amin and Sherif, 2001; Ashour
et al., 2007; Amin et al., 2009a,
The sewage sludge production is continuously increasing in Egypt. Therefore, the main current pressing needs are to find and develop more efficient sustainable technologies to allow a safe and suitable reuse of sewage sludge in agriculture. Furthermore, the legislations should be more adapted to Egyptian conditions as well as improvement of the institutional capacity to guarantee the enforcement of their application.
In vivo and in vitro, higher plants function as biosensors of
pollutants. Plants are able to give repeatable and quantifiable responses. The
biological assay-guided chemical analysis (the association between biological
and chemical approach) is the best way to obtain information about the kind
of polluting agents, their origin and fate in environment and living organisms.
The choice of pollen mother cells of corn as biosensors of pollutants causing
mutations in crop plants has advantages in that very large number of pollen
grains can be obtained from one tassel. Each kernel arising from treated pollen
is potentially heterozygous for a unique induced mutation that can be expressed
immediately (if dominant) or in the progeny of the M1 (if recessive).
Plewa (1982) recommended that Zea mays bioassays
can be used to assess genotoxicity from potential chemical and environmental
pollutants. From the many meiotic mutants described in plants and other organisms,
it is obvious that meiosis is controlled by a large number of genes (Chaudhury
et al., 1992; Bhatt et al., 2001),
the knowledge of which is mainly restricted to their cytological and genetic
This study provides information to help answer questions and evaluate the option
of using municipal sewage water and sludge instead of chemical fertilizers.
Therefore, the aim of this work was to monitor the in situ genotoxic
and cytotoxic potentialities of maize grown on agricultural soil having residual
sewage sludge. The chemical composition of the used sewage sludge was carried
out by Amin and Sheriff (2001). Using the second generation
of treated Zea plants and comparing its net results with (Amin
et al., 2009a) who stated that some heavy metals accumulation in
leaves and grains (Cu, Zn, Cd, Pb) as a result of residual sewage sludge treatments
may lead to genotoxicity through affecting the genes responsible for some Zea
yield parameters and kernel characters.
Analysis of the clastogenic effects of metals and their compounds on higher
organisms indicates some general trends by Sharma and Talukder
(1987). Following chronic exposure to subtoxic doses, a decrease in mitotic
frequency and increase in chromosomal abnormalities were observed. These effects
are usually directly proportional to the dose applied and the duration of treatment
within the threshold limits. Recovery after acute treatment is inversely related
to the dosage. The ultimate expression of the effects depends on the test system
used. In plants, the solubility of the metals in water is of much greater importance.
The degree of dissociation of metallic salts and the rate of absorption affect
significantly the frequency of chromosomal aberrations. Therefore, evaluation
toxic metal levels can be assessed and compared by Joint Expert Committee on
Food Additives (JECFA) of the Food and Agriculture Organization of the Joint
Nations and the World Health Organization United Nations and the World Health
Organization International Programme on Chemical Safety FAO
and WHO (2000, 2001).
MATERIALS AND METHODS
The present study was carried out at the field station of faculty of agriculture,
Alexandria University. Composted sewage sludge was obtained from Alexandria
General Organization of Sanitary Drainage (AGOSD) of Alexandria city in February,
1999. The chemical composition of sludge and physical and chemical characteristics
of the soil were determined according to (Page et al.,
1982) and are presented by Amin (2001). A field
experiment was carried out in 1999 to evaluate the effect of residual sewage
sludge, one and two additions on M1 yield parameters of Zea mays
L. variety H320 (Amin et al., 2009a). Several
rates of sewage sludge were used (0, 10, 20, 30 and 40 T/F). During this experiment,
immature male tassels at the boot stage (~about eleven weeks old Zea) were collected,
from six different plants from each treatment and fixed immediately in fresh
solutions of ethanol: glacial acetic acid (3:1, v/v). Semipermanent acetocarmine
and acetooreicin meiocytes preparations were examined. Pollen Mother Cells (PMCs)
at different meiotic stages were screened and various chromosomal and cellular
irregularities were recorded.
The percentage of aberrant PMCs for each treatment was calculated as the number of aberrant PMCs/total number of cells, while the percent of each aberrant type was calculated as the number of one type of aberrant PMCs/total number of examined PMC's in each treatment. The number of aberrations per PMCs was calculated as total kinds of aberrations/total number of aberrant PMCs. The Percentage of sterile pollen grains was also estimated using acetocarmine stain and calculated from total examined pollen grains.
Statistical analysis: Statistical analysis of data was carried out using the one-way Analysis of Variance (ANOVA) and significant differences between the means were assessed by Duncans multiple comparison tests at p = 0.05.
where, n is the sample size (total number of pollen mother cells) and X the percent of aberrant pollen mother cells.
RESULTS AND DISCUSSION
In the present study an appreciable number of meiotic aberrations were recorded in pollen mother cells of M2 plants grown on soil having residual one and two additions with different rates of sewage sludge- 0, 10, 20, 30 and 40 T/F (Table 1-3, Fig. 1, 2).
||Percentage of aberrant stages of M2 meiocytes of
plants grown on soil with one and two residual sewage sludge addition (calculated
from Total meiocytes)
Frequency of aberrant meiocytes and meiotic phases: Generally, the percentage
of aberrant mother cells increased significantly by either residual one or two
residual sludge addition. The mean percentage of aberrant mother cells increased
about three folds than the control with increasing sewage sludge concentration
by residual one and/or two additions, except 20 T/F residual one addition (Table
1). This lowest percentage of aberrations of 20 T/F could be attributed
to the high content of organic matter in respect to heavy metals present in
this low rate of sludge (Sang and Li, 2002). Organic
matter ability to sequester most heavy metals found in soil and sludge lowered
their cytotoxic effect. This agreed with Ashour et al.
(2007) using wheat as a plant bioassay. However, the mean aberration percentage
in both treatments indicated that the residual two additions treatments were
more cytotoxic than residual one addition (20.06 and 15.96, respectively). The
percentage of aberrant PMCs at meiotic Division two (DII) caused by residual
two additions were three times higher than those at meiotic Division one (DI).
The most stage of aberrations of DI was restricted to metaphase in all treatments
while, aberrant end product formed the most frequent stage in DII. These are
all different products than the normal tetrad stage. It amounted to six to ten
times higher than those of the control.
Aberrant meiocytes contained about 1.1 kinds of aberrations per PMC for all treatments (Table 2). The highest kind of aberrations in division I was abnormal chromosome distribution which appeared in metaphase I as absence of spindle microtubules or abnormal chromosome movement (precocious, laggards) and unequal polar groups (Fig. 1). These kinds were more frequent in the 10T/F than the other treatments. Sticky figures were induced by all residual one addition and 10T/F residual two additions treatments. In the same time, the percentage of sticky chromosomes increased by increasing sludge concentrations except 20 T/F induced the lowest value (1.6%). Generally, abnormal spindle behavior either inhibition or microtubule orientation and irregular chromosome movement decreased by all sludge treatments except 10 T/F two additions. Prophase one with two nuclei, less or more bivalent number and fragmented bivalents at diakinesis appeared in control and all residual one addition and 10 T/F residual two additions treatments. Telophase cells with protrusion at the position of cell plate were induced only by 10 and 30 T/F in division I and 30 and 40 T/F in division II residual one addition.
||The percentage of aberrant end products of aberrant M2 Meiocytes
of plants grown on soil with one and two residual sewage sludge addition
(calculated from aberrant meiocytes)
||M2 Meiocytes of Zea mays at DI and II with
different kinds of aberrations: (a): Pachytene with two nuclei, (b): Diakinesis
with fragmented and less bivalent number, (c): C-Metaphase I, (d): Metaphase
I with precocious chromosomes, (e): Metaphase I with laggard, (f): Anaphase
I with laggard chromosome, (g): Anaphase I with bridges, (h): Asynchronized
cell, (i): Overlapped and asynchronized cell, (j and k): Telophase II with
Protrusions at the position of cell plate, (l): Metaphase II with abnormal
chromosome orientation and cell contour, (m-o): different degrees of overlapping
and abnormal cell orientation
The highest kind of aberrations in division II was induced by one-addition treatments. Division II meiocytes contained high percent of overlapping cells and abnormal cell contour with highest value induced by 20T/F two additions. The highest percentage of asynchronized cells and telophase cells with protrusion at the position of cell plate occurred after 30T/F one addition.
However, while abnormal cell contour, abnormal chromosome orientation and sticky figures were found in sludge treatments only, high percent of abnormal chromosome movement was found in control and decreased to very low values by some sludge treatments.
In the present study, although all flower buds were collected from all treatments
at the same time, the highest sludge rates (30 and 40 T/F) of the residual two
additions were found to be pollen grains only in addition to the absence of
meiotic end product in 40 T/F treatment. This may be suggested that residual
sludge enhanced the rate of meiotic division leading to the enhancement of maturity
of zea plant (earliness). Similar result was found by Ashour
et al. (2007) using wheat plant.
Cytological events of meiosis are controlled by a large number of genes acting
from pre-meiosis to the post-meiotic mitosis. Natural and induced mutations
that affect many steps of the process have been widely described in maize and
other species (Golubovskaya, 1989). Therefore, mutations
of these genes may cause anomalies that impair plant fertility (Ricci
et al., 2007; Kaul and Murthy, 2004).
In the present study, chromosome stickiness might be due to a recessive gene
mutation resembling that discovered in maize by Beedle (McGill
et al., 1974), ending with immediate reactions with DNA causing DNA-DNA
or DNA-protein cross linking (El-Kodary et al., 1990;
El-Ghamery et al., 2000; Kovaleva,
2008). Gaulden (1987) postulated that sticky chromosomes
may result from the defective functioning of one or two types of specific non-histone
proteins involved in chromosome organization which are needed for chromatid
separation and segregation. The altered functions of these proteins leading
to stickiness may be caused by mutations in the structural genes coding for
them (hereditary stickiness) or by the action of mutagens on the proteins (induced
stickiness). According to Kumar and Rai (2007), it seems
most probable that the heavy metals may have caused some kinds of gene mutations
which led to incorrect coding of some non-histone proteins involved in chromosome
In the present study, residual sewage sludge reduced the percent of chromosomes
not able to congregate in the metaphase plate, remaining scattered in the cytoplasm.
Absence or defective spindle fibers or defects in kinetochore that impair spindle
fiber attachment could be responsible for such abnormality. A mutation involving
absence of spindle fibers and causing inability of bivalent congression at the
metaphase plate was reported in maize by Daniela et al.
(2005) and might be inhibited by residual sewage sludge.
Many factors of both cytoplasmic and nuclear origin could influence spindle
formation and chromosome alignment. Dysfunctional cytoplasm could lead to formation
of abnormal meiotic spindles and induce chromosomal mal-segregation (Battaglia
et al., 1996; Gaulden, 1992; Lin
and Keefe, 2004). Mutations controlling chromosome segregation have been
described in maize, among them, the dv (Clark, 1940),
ms43 (Golubovskaya and Sitnikova, 1980), ms28 (Golubovskaya
and Distanova, 1986) and ms17 (Albertsen and Phillips,
1981) genes. The dv, ms28 and ms43 mutants cause failure of the spindle
or impair disjunction mechanisms (Golubovskaya, 1979).
Under the action of the dv gene (Clark, 1940; Staiger
and Cande, 1990), the spindle fibers lie parallel or diverge instead of
converging toward the poles (Caetano-Pereira and Pagliarini,
2001). This may lead to abnormal spindle orientation which might be inhibited
by residual sewage sludge.
Staiger and Cande (1991) stated that all anomalies
of chromosome segregation and cytokinesis are dependent on a delay of spindle
fiber depolymerization (which in normal meiosis begins after anaphase I) affected
by the ms28 gene and consequently leading to abnormal chromosome segregation
(i.e., karyokinesis or abnormal chromosome movement) in division II.
Golubovskaya and Distanova (1986) suggested that the
dv mutant affecting meiosis after metaphase I mainly disturbs the orientation
of the two spindles relative to each other at meiosis II, leading to abnormal
orientation of spindle fibers within the spindle, ending with abnormal spindle
The forces required for spindle assembly and movements of the spindle and chromosomes
is initiated at Microtubule Organizing Centres (MTOCs) and have been attributed
to microtubule dynamics, together with microtubule motors (Endow,
1999). In higher plant meiocytes, microtubules initially appear around prometaphase
chromosomes, indicating a chromatin-mediated spindle assembly mechanism (Chan
and Cande, 1998), however Mei mutations was found to disrupt the structure
and function of spindle (Staiger and Cande, 1990; Staiger
and Cande, 1991; Golubovskaya et al., 1992;
Shamina et al., 1994; Mendes-Bonato
et al., 2006).
Macieira-Coelho (2007) stated that disturbing the polarity
of cells affects the orientation of the cell division plane. Accordingly, asymmetric
division or overlapping cells in division II could occur. The presence of telophase
cells in meiosis I and II with a protrusion at the position of cell plate may
be due to the effect of the Preprophase Band (PPB) at the plane in which a cell
will divide (PPB: microtubules in the outer cytoplasm become concentrated into
a ring). These cortical microtubules oriented in the same plane as the future
PPB, indicate cell division plane (Fig. 3). Division planes
in the mutants appear random from the earliest stages of embryogenesis onward
and hence the orientation of cell division is severely affected. The PPB is
not the single decisive cue for orientation of the spindle; the spindle axis
may rotate during division due to space constraints. So, a new division site
may be chosen, resulting in a change of the orientation of cell division.
Abnormal cell contour and/or cell wall protrusion were detected in high percentages
in meiocytes after 20 T/F of two residual sewage sludge treatment. This might
be attributed to the drastic changes in deposition of uniform cell wall components
leaving weak areas where protrusions occur and abnormal cell contour (Meijer
et al., 1988).
The different kinds of aberrant meiotic end products (Fig. 2) were divided into three categories according to the number of microspores resulting from one meiocyte (diad and triad), arrangement of microspores within meiocytes wall (overlapped, decussate, linear, Apple, T, J, X, V -Shaped and abnormal cell orientation) and structural malformations as meiocytes having appendages and cytoplasmic protrusions. The percentage of aberrant meiotic end products increased by residual one than two additions (Table 2) and its value were more than thirty and eleven times than the control. When the meiotic end product aberrations were calculated from total end products only (normal tetrad stage) (Table 3), it was found that its percentage decreased by increasing residual sludge rates, this means that, 10 T/F, residual one addition caused the highest value.
According to Albertsen and Phillips (1981), the ms17
gene presents variable expression that affects spindle formation causing a variety
of quartet abnormalities, including coenocytic quartets and structures with
more or less than the normal four microspores. As a consequence, synchronous
behaviour leads to the formation of a wide range of meiotic products, from diad,
triads and tetrads with uneven-sized microspores (Risso-Pascotto
et al., 2003; Reginaboldrini et al., 2006).
Also, the total lack of a spindle may have been due to the absence of microtubules
which are needed for spindle-fiber formation (Caetano-Pereira
and Pagliarini, 2001).
||Abnormal meiotic end product of M2 Meiocytes of
Zea mays. (a and b):different degrees of overlapping tetrads, (c):
abnormal T-shape orientation, (d and e): different degrees of Linear tetrad,
(f): Linear Triad, (g): Diad and (h): Tetrad with cytoplasmic protrusion
In the mean time, the two cytoskeletal elements of spindle, microtubules and
microfilaments, were found by Staiger and Cande (1991)
to interact in a cell cycle-specific and site-specific fashion during higher
plant meiosis leading to severa1 meiotic mutants known to have stage-specific
disruptions in their microtubule arrays. Herein, abnormal cell contour, cell
wall appendage, cytoplasmic protrusions and abnormal meiotic end products could
be the result of a similar mutation. In addition, conditions of polyspory have
been observed to depend on the direction of the formation and the number of
cell plates resulting from several spindles (Caetano-Pereira
and Pagliarini, 2001). Also, Golubovskaya and Distanova
(1986) suggested that the presence of "dv" mutant mainly disturbs the orientation
of the two spindles relative to each other at meiosis II leading to abnormal
meiotic end product arrangements. This also may lead to the formation of abnormal
arrangements of microspores within meiocyte wall as decussate, linear, T- J-
X- Z-Apple- shape, overlapped and other abnormal cell orientation found in the
Due to the effect of residual sewage sludge for the maturation, the pollen
grains formation was inhibited after 10, 30 and 40T/F residual one addition
and 10T/F residual two addition in the time of immature male tassels collection
(~about eleven weeks old Zea).
|| PPB predicts the orientation of cell division selected
||The percentage of aberrant end products and the different
kinds of aberrant M2 microspores meiocytes
Pollen grain sterility indicated that the treatments of residual second additions
ranged from 9-13%. However, no pollen grains were detected in the residual one
addition except 6.23% in 20% T/F (Table 1). All previous values
ranged from 3-8 times that of the control. The trend of the occurrence of aberrant
meiotic end products was approximately similar to the percentage of pollen grain
sterility. Inspite of that, the productivity, represented as kernel index, of
these treatments were not significant difference when compared with the control
(Amin et al., 2009a).
Generally, single metal or combination of metals have differential mode of action in biological system, since Metal-metal interaction plays a vital role in health and toxicity. Therefore, it is important to discuss mode of action of heavy metal(s) that is taking part in generating the genotoxicity in the present study.
Peijnenburg and Vijer (2007) recorded a variety of
mechanisms exist for the detoxification of metals once they have entered an
organism, precluding simple predictions of metal-induced toxicity on the basis
of metal quotas, as occur with organic contaminants. Metals inside organisms
can be present in the free ionic form or as soluble salt, or bound as follows:
||In the active center of functional proteins and low molecular
weight peptides (as Zn finger proteins)
||In the active center of enzymes (as cytochrome)
||To transport proteins (as ferritin)
||To metallothionine (MT) or other sequestration proteins
||To cellular constituents causing dysfunction (as ion channels,
The interactions among metals and between metals and plant are numerous and
occur commonly during the processes of absorption and sequestration (Peijnenburg
and Vijer, 2007).
Mode of action and toxicity: Most trace metals mediate gene expression
by activation of single transduction pathways. Signal transduction is a progression
by which information from an extracellular indication is transmitted into the
cell through the plasma membrane and along an intracellular sequence of signaling
molecules to excite a cellular response. The response may be the commencement
of a gene transcription that occurs through various regulatory proteins that
bind to specific DNA sequences in a gene. The net result of this binding is
usually transcription of that gene and is referred to as transcriptional activation
Mode of action of Zn: The cytotoxic effects of zinc on plants are elucidated
by Rout and Das (2003) as the major change was seen
in the nucleus. If two metals bind to the same site of toxic action (such as
competition of Zn2+ and Cd2+ for Ca2+ transport
sites), it is possible to model the total metal bound to that site and hence,
to predict metal toxicity using a mechanistic receptor binding approach in a
concentration additive model. Alternatively, if two metals do not complete for
the same binding site (such as binding of Zn2+ to Ca2+
transport sites vs. simultaneous binding of Cu2+ to Na2+
transport sites) then these models may provide more reliable estimates of individual
metal bioavailability which then can be combined in more accurate response additive
models (Peijnenburg and Vijer, 2007).
||Mode of action of Cd: Cell cycle progression, DNA replication
and repair differentiation, proliferation and apoptotic pathway are altered
and affected by cadmium. By activation cellular signals, it regulates cell
cycle progression and inhibition of DNA methylation and/or interference
with cell adhesion. Although, it enhances DNA synthesis and cell proliferation
at lower concentration than 1 μM, Cd exposure above this concentration
inhibits DNA synthesis and cell division (Yang et
al., 2004). Zn-dependent proteins and Zn-binding molecules are candidate
targets of Cd+2 toxicity. Cd2+ can replace Zn and
so interfere with some of many reliant processes (Weber
et al., 2006)
||Mode of action of Lead: Possible mechanism for lead
toxicity includes completion with and substitution for calcium, disturbance
of calcium homeostasis. Calcium blocks the uptake of lead because it is
a strong blocker of calcium channels. Disturbance of tissue oxidant/antioxidant
balance and substitution or zinc in various Zn-mediated processes are some
of the metabolic repercussions of lead toxicity (Ahmed
et al., 2007). Therefore, lead can alter the regulation of genetic
transcription through sequence-specific DNA-binding zinc sites in receptor
channels (Langman and Kapu, 2006)
||Mode of action of Copper: Copper can induce oxidative stress. Toxicity
associated with Cu may be due to oxidative damage to biological macromolecules
(Peijnenburg and Vijer, 2007)
Therefore, due to sewage sludge production is continuously increasing in Egypt, the main current pressing needs are to find and develop more efficient sustainable technologies to allow a safe and suitable reuse of sewage sludge in agriculture. Furthermore, the legislations should be more adapted to Egyptian conditions as well as improvement of the institutional capacity to guarantee the enforcement of their application.
In sludge rule, it is stated that limits of the annual and cumulative loading of trace elements are adequate to protect against phytotoxicity and to prevent the accumulation of these elements in crops at levels harmful to consumers if it is applied in quantities commensurate with crop needs. Nevertheless, continued monitoring of trace elements in soils over longer time periods must be carried out. However, heavy metals and toxic compounds could be reached to higher levels in the course of time by repeated applications of sludge at agronomic rates and thus it could be inevitable to meet the irreversible problems of cumulative loading of trace elements and in any type of soil in long-term effect.
This work provides a bioassay to investigate the mutagenic properties of soil amended with sewage sludge. In the present study, the total percentage of aberrant pollen mother cells increased significantly with increasing sewage sludge concentration of residual one or two additions. A large number of genes acting from pre-meiosis to the post-meiotic mitosis could be affected, inducing mutations of these genes, may cause anomalies that impair plant fertility.
Therefore, to keep soils clean for future generations it is absolutely necessary to lower heavy metal limits in soils and organic materials.
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