United States
 Environmental Protection
 Agency
Health Effects Research
Laboratory
Research Triangle Park NC 27711
 Research and Development
EPA/600/S1 -85/022 Jan. 1986
 Project Summary
 Investigation  of  Parasites  in
 Sludges and  Disinfection
 Techniques
 R. S. Reimers, M. D. Little, A. J. Englande, Jr., D. B. McDonell,
 D. D. Bowman, and J. M. Hughes
  The objectives of this research grant
were to: 1) assess the presence and
densities of resistant stages of para-
sites in municipal wastewater sludges
(sewage) in northern  United States;
2) compare the results of this study
with the results of our previous study of
sludges in southern United States;
3) evaluate several decontamination
techniques for their effectiveness in in-
activating parasites in  waste sludges;
and 4) develop a standard method for
the parasitologic examination of waste
sludges. Sludge samples  from all
phases of treatment (i.e., primary, etc.)
were collected during the fall, winter
and summer from 48 municipal waste-
water treatment plants located in New
York (13 plants), Ohio (12  plants), Min-
nesota (11 plants), and Washington (12
plants).  Resistant stages of twenty
types of parasites were found in these
samples which may represent 25 to 30
different human and animal parasites.
  This Project Summary was devel-
oped by EPA's Health Effects  Research
Laboratory, Research Triangle Park, NC,
to announce key findings of the re-
search project that is fully documented
in a separate report of the same  title
(see Project Report ordering informa-
tion at back).

Introduction
  The problems associated with the oc-
currence of human and  animal  para-
sites in  domestic wastewater sludges
have received little attention in the
United  States prior to  1970.  Even
though studies had examined waste-
water effluents and sludges from mu-
nicipal treatment plants in  different
parts of the country and had found the
eggs of several intestinal helminths,
these studies have little practical value
other than recording the presence of the
parasites found, since  the techniques
used to recover the parasites and to
quantitate them varied from study to
study.
  In a recent study for the U.S. Environ-
mental Protection Agency (EPA) by Tu-
lane University, "Parasites in  Southern
Sludges and Disinfection  by  Standard
Sludge Treatment," the presence and
densities of parasites in  sludge samples
from 27 municipal wastewater plants in
Florida, Alabama, Mississippi, Louisi-
ana, and Texas were investigated over
one year,  and  several  standard proc-
esses were evaluated in regard to their
effectiveness in inactivating parasites.
The results indicated that further testing
was required to develop reliable ap-
proaches to the inactivation of parasites
in  municipal sludges,  and that addi-
tional information on the occurrence of
parasites in sludges in other areas of the
United States  was needed before the
potential health risks associated with
the land application of  wastewater
sludges could be judged.
  The purpose  of the present study was
to determine the types and densities of
parasites in sewage sludges in northern
United States, to evaluate factors which
may affect their densities in final
sludges, i.e., sludges destined for final
disposal, and,  through  laboratory ex-
periments to determine the  effective-
ness of several sludge treatment proc-
esses in inactivating parasites.

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  Field studies consisted of collecting
sludge samples representing all phases
of the treatment process (primary stabi-
lization, post-stabilization,  etc.) during
the fall, winter and spring seasons, re-
spectively, from  48 municipal waste-
water treatment plants located in New
York (13), Ohio (12), Minnesota (11) and
Washington (12).  Plants of four size cat-
egories, <1  MGD,  1-10 MGD, 10-50
MGD, and >50 MGD, were included in
the study. Each sample  was analyzed
for parasites and several abiotic param-
eters, i.e., pH, temperature, total sus-
pended and volatile solids, etc. In labo-
ratory studies, aerobic digestion, lime
and caustic stabilization, ammonifica-
tion, irradiation with cobalt 60 and ultra-
sonification  were investigated  regard-
ing their effectiveness  in  inactivating
parasites in municipal sludges.

Results

Field Studies

Parasitological Findings
  In sludge  samples collected from
each of the  48 treatment plants in the
four northern states, 20 different types
of parasite eggs or cysts  were detected
(Table 1), but many of them could be
identified to  the genus level only. Ap-
proximately 90%  of all sludge samples
examined contained stages of one  or
more parasites.  The four most com-
monly found parasites  were Ascaris
spp., Trichuris trichiura, Trichuris vulpis
and Toxocara spp. The eggs of one or
more of these four parasites were found
in about 89% of the samples examined
from  the four states. The geometric
means of the numbers of eggs per  kg
dry weight of sludge of  each of these
four parasites found in different types of
sludge samples from the four states and
the percentages of samples positive for
these parasites are presented in Table 2.
The percentages  of treatment plants in
the four states with samples positive for
these eggs are shown in Table 3.
  Ascaris eggs were found in a higher
percentage of samples  in  Washington
than in the  other three states and  the
mean number of eggs was also higher
in Washington sludges.  7. trichiura
eggs  were found more commonly in
New York than in the other three states.
7.  vulpis eggs were found  in more
sludge samples in Ohio and New York,
but the egg densities did not differ sig-
nificantly in the  sludges in the four
states. Toxocara eggs were the most
frequently found parasite with viable
Table 1.    Parasites Found in Sludge Samples from 48 Municipal Plants in Northern
          United States
      Parasite Found
     Probable Identity
                                                              Definitive Host
Ascaris eggs

Toxocara eggs

Trichuris trichiura eggs

Trichuris vulpis eggs
Toxascaris-//te eggs
Parascaris equorum eggs
Ascaridia-Wce eggs

Gongylonema-//fce eggs

Physaloptera-//7re eggs

Trichosomoides-//fce eggs

Capillaria spp. eggs (3 or
more types)
Hymenolepis diminuta eggs
Hymenolepis nana eggs
Hymenolepis sp. eggs

Diphyllobothrium-/;7re eggs

Spirometra-Mce eggs
Schistosoma mansoni
egg (1)
Entamoeba coli-like cysts

Giardia cysfs

Coccidia oocysts
Ascaris lumbricoides'
Ascaris suum
Toxocara canis2
Toxocara cat!2
Trichuris trichiura
Trichuris suis3
Trichuris vulpis
Toxascaris leonina
Parascaris equorum
Ascaridia galli
Heterakis gallinae
Gongylonema neoplasticum
Gongylonema pulchrum
Physaloptera spp.
Turgida turgida
Trichosomoides crassicauda
Anatrichosoma buccalis
Capillaria hepatica
Capillaria gastrica
Capillaria spp.
Capillaria spp.
Hymenolepis diminuta
Hymenolepis nana
Hymenolepis spp. (poss.
more than one species)
Diphyllobothrium latum
Diphyllobothrium spp.
Spirometra mansonoides
Schistosoma mansoni

Entamoeba coli4
Entamoeba spp.
Giardia lamblia
Giardia spp.
Isospora spp.
Eimeria spp.
'Eggs of A. lumbricoides and A. suum are indistinguishable.
2Toxocara eggs were probably mostly T. canis.
3T. suis eggs were probably only rarely seen.
4An intestinal amoeba that is a commensal, not a parasite.
Humans
Pigs
Dogs
Cats
Humans
Pigs
Dogs
Dogs and cats
Horses
Domestic poultry
Domestic poultry
Rat
Cattle, pigs, etc.
Dogs, cats, etc.
Opossums
Rats
Opossums
Rats
Rats
Birds
Wild mammals
(opossums, racoons,
etc.)
Rats
Humans and rodents
Domestic and/or wild
birds
Humans, dogs, bears
Dogs, bears, birds
Dogs and cats
Humans

Humans
Rodents, etc.
Humans
Dogs, cats, mammals
Dogs, cats
Domestic and wild
birds, mammals
eggs being found in one or more sam-
ples from each plant studied (Table 3).
The densities of Toxocara eggs were
considerably lower  in samples  in
Minnesota than in samples in the other
three states.

Parasite Densities vs. Popula-
tion Served by Plants
  Utilization  of  multiple regression
analysis to examine the relationship of
the population served by the waste-
water treatment plants to the densities
of total and viable Ascaris and 7. trichi-
ura eggs  in undigested  sludges were
not related to the size of the population
served by the plant;  however, the densi-
ties of total and  viable  7. vulpis and
Toxocara  eggs decreased significantly
           in the undigested sludges from north-
           ern (and/or southern) states as the pop-
           ulation served by the treatment plants
           increased. In digested sludges, the den-
           sities of viable and total Ascaris and 7.
           trichiura eggs  increased significantly
           with an  increasing population size,  but
           the densities of viable  7. vulpis eggs
           and viable total Toxocara eggs were not
           significantly related to  the population
           served.
           Parasites in Stabilized Sludges
             In general, no differences were noted
           in the densities of eggs in aerobically
           and anaerobically digested sludges ex-
           cept for viable Ascaris and Toxocara
           eggs. Significantly lower densities of vi-

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Table 2,   Ascaris spp., Trichuris trichiura, T. vulpis and Toxocara spp. Eggs in Samples of Undigested Sludge from Digesters

                                                             PARASITE
Source or
Type of Sludge
Undigested
N= 162
% positive
Geometric Mean2
Digester
N= 137
% positive
Geometric Mean2
Post-Digestion
A/= 773
% positive
Geometric Mean2
All Sludges
N= 142
% positive
Geometric Mean2
Ascaris spp.
Total1 Viable


51%
940


56%
1700


54%
560


54%
WOO


49%
670


50%
1400


45%
310


48%
710
Trichuris trichiura
Total1 Viable


35%
500


42%
480


29%
260


36%
440


27%
650


28%
400


19%
130


25%
400
T. vulpis
Total1 Viable


33%
430


48%
460


47%
240


42%
400


31%
440


45%
440


37%
190


37%
370
Toxocara spp.
Total1 Viable


81%
880


85%
1200


69%
330


79%
880


78%
870


74%
740


50%
190


69%
670
 1 Viable and nonviable eggs.
 2Antilog of the mean of the log of positive samples, expressed as number of eggs/kg dry weight of sludge.
Table 3.
Parasite
Ascaris
T. trichiura
T. vulpis
Toxocara
Percentage of Plants in Four Northern States with
trichiura, T. vulpis and Toxocara.
Viable and Nonviable Eggs
85%
88%
85%
100%
Eggs of Ascaris, Trichuris
Viable Eggs
77%
73%
81%
100%
able Ascaris and Toxocara eggs were
found  in  anaerobically  digested
sludges.

Parasites in Drying Beds
  In all  cases a significant relationship
between the density of viable eggs and
the moisture content of the sample was
observed. As the moisture content de-
creased, the densities of viable parasite
eggs decreased.
  Step-up multiple regression  analysis
was applied to the density of viable
eggs in drying  beds vs. the  density of
viable  eggs  in a simultaneously col-
lected  sample  of undigested  sludge.
The purpose was to test the significance
of the  effects of the percent moisture
content of the drying bed, the age of the
sludge  in the bed, the season of the
sampling,  and the type of digestion
process before the drying bed.
  With additional controls for the age of
the sludge, season of collection  and
type of digestion, the percent moisture
content of the  drying bed  sludge was
not found to be significant with respect
to densities  viable Ascaris  eggs,  al-
though it was significant for densities
Tbxocara eggs (p < 0.001). Fewer viable
Toxocara eggs were found with de-
creasing sludge moisture content. The
age of the sludge in the drying bed was
not found to have a significant effect for
either Ascaris (0.25 > p > 0.10) or Toxo-
cara (p > 0.25) eggs. The type of diges-
tion process was not significant with  re-
spect to Ascaris  (p > 0.25)  but was
significant with respect to Toxocara
eggs (0.05 > p > 0.01) with fewer viable
eggs in the drying  bed associated with
anaerobic processes than with aerobic.
Significantly,  fewer Ascaris eggs were
found  in  fall  than in  winter
(0.05 > p > 0.01), while no seasonal dif-
ferences were found for Toxocara eggs.
Well over half of all simultaneously col-
lected samples showed more than 75%
fewer viable  Ascaris, T. trichiura,  T.
vulpis and Toxocara eggs in drying bed
samples than in digester samples. Only
five samples from the northern drying
beds  had a moisture content of less
than  20%, which was previously re-
ported to be necessary for effective par-
asite  egg inactivation.  Three of these
samples were from covered drying
beds; while the other two samples were
from  plants  in eastern Washington.
  Higher densities of viable Ascaris
eggs in undigested sludges were signif-
icantly associated with higher densities
of viable Ascaris eggs  in drying bed
sludges (p = 0.001). This  was also true
for the eggs of  T.  trichiura (p < 0.03)
and T. vulpis (p < 0.03). The densities of
viable Toxocara  eggs did not show  a
significant relationship, however.

  Step-up multiple regression analysis
was utilized to test the significance of
the effect of  1) percent moisture content
of the drying bed sludge, 2) age of the
sludge in the bed, and 3) digestion proc-
ess (aerobic vs.  anaerobic)  employed
on the undigested sludge on the inacti-
vation of parasites. No trend was noted
for sludge age and the digestion proc-
ess, but decreasing moisture content of
the drying bed sludge was significantly
associated with decreased densities of
viable Ascaris (0.01 >p> 0.001),  7.
trichiura(Q.Qb >  p > 0.01),  T.  vulpis
(p < 0.001)  and  Toxocara (p < 0.001)
eggs.

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Sludges Destined for Ultimate
Disposal
  The type of sludge destined for dis-
posal was dewatered sludge  in 31
plants,  liquid sludge (primary or di-
gested) in 13 plants, and both de-
watered and liquid sludge in 4 plants. In
the majority  of cases, the sludge was
land-applied with only about one-third
being placed in landfills, lagoon stor-
age, or  the ocean.

  The percentages  of the samples  of
these final sludges that contained viable
eggs of  Ascaris, T. trichiura, T. vulpisor
Toxocara and the geometric mean  of
these eggs are presented by  state  in
Table 4. In samples from all four states,
Toxocara eggs were found most fre-
quently (55%), with Ascaris eggs,  7.
vulpis eggs and 7. trichiura eggs  being
found somewhat  less frequently, 48%,
38% and 22%, respectively.  Ascaris
eggs occurred in  higher levels in final
sludges than the  other three parasites,
and the densities of Ascaris eggs in final
sludges in Washington  were signifi-
cantly higher than in these sludges in
the other three states.
  The number of plants that distributed
sludge to the  public for use at home in-
cluded five in Ohio, four  in New  York,
two in Washington,  and one in Minne-
sota. Viable eggs of Ascaris, T. trichi-
ura, T. vulpis and Toxocara were found
in 39%,  6%, 56% and 50%, respectively,
of the samples of these sludges. The ge-
ometric means of  viable eggs of each of
                    these parasites found in positive sam-
                    ples were 492, 92, 300 and 580 eggs/kg
                    dry weight, respectively.


                    Laboratory Studies
                      Continuous aerobic digestion at 25°C
                    with detention times  of 10, 20 and
                    30 days did not noticeably affect the vi-
                    ability of Ascaris eggs in the sludge.
                    However, when digestion was carried
                    out at 35°C, a 30-50 percent inactivation
                    of the eggs was noted within 10 days.
                      The addition of caustic (NaOH) to
                    sludge previously digested at 25°C had
                    little effect on the viability of the Ascaris
                    eggs, even over a period of 10 days.
                    However, when caustic was  added to
                    sludge from  the 35°C digester, 97% of
                    the eggs were killed  within 5 days and
                    100% were killed within 10 days. In lime
                    stabilization studies, no effect on the As-
                    caris eggs was noted until  a  lime
                    dosage of 1,000 mg lime per gram of
                    sludge solids was used. At that dosage,
                    97% of the  eggs were killed within
                    5 days.

                     When ammonium sulfate at a dosage
                    of 50 mg ammonia per gram of sludge
                    solids was added to  sludge previously
                    aerobically digested at 25°C for 10 days,
                    there was little effect  on the Ascaris
                    eggs during  the first five days. After
                    10 days, 62% of the  eggs were inacti-
                    vated. When the ammonia dosage was
                    increased to 500 mg/gram solids, com-
                    plete or near  complete inactivation was
                    observed  after 10 days.
                                               When ammonia gas was added to
                                             sludges previously aerobically digested
                                             at 25°C at detention times of 10,20 or 30
                                             days, a dosage of one percent was nec-
                                             essary to obtain effective inactivation of
                                             the Ascaris eggs. When ammonia was
                                             added to  sludges digested at 35°C, a
                                             higher degree of inactivation was found
                                             to occur than with comparable dosages
                                             in sludges digested at 25°C.
                                               The exposure of Ascaris eggs to an
                                             ultrasonic field at 33  KHz and 600 watts
                                             for 11 minutes inactivated 77 percent of
                                             the eggs.

                                               In studies using gamma radiation
                                             from  a Cobalt 60 source, it was found
                                             that a dosage of 200 Krads or greater
                                             was completely  effective in killing As-
                                             caris eggs in sludge (3% solids). Eggs
                                             from the feces of pigs and from the uteri
                                             of worms were  equally susceptible to
                                             the radiation, as were the intact and de-
                                             coated eggs.
Table 4.    Percentage of Sludge Samples Destined for Disposal in Each of Four Northern
          States that Contain Viable Eggs of Ascaris, Trichuris trichiura, T. vulpis and
          Toxocara and Mean Number of Eggs of Each Parasite
                                      STATE
     Eggs
MN
OH
                                              NY
                                        WA
           All
        Samples
Ascaris
% positive           49%
Geometric Mean'     375

T. trichiura
% positive           14%
Geometric Mean      140

T. vulpis
% positive           12%
Geometric Mean      255

Toxocara
% positive           51%
Geometric Mean      315
             41%
             235
             12%
             150
             63%
             270
             280
             49%
             560
             31%
             390
             56%
             230
             49%
             455
47%
1920
33%
 280
28%
 395
50%
 515
48%
565
22%
265
38%
270
55%
370
1Antilog of the mean of the log of positive samples; expressed as number of eggs/kg dry
 weight of sludge.
                                                                        S. GOVERNMENT PRINTING OFFICE: 1986/646-116/20763

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     R. S. Reimers, M. D. Little, A. J. Englande. Jr., D. B. McDonell, D. D. Bowman, and
      J. M. Hughes are with School of Public Health and Tropical Medicine, Tulane
      University, New Orleans, LA 70112.
     Norman E. Kowal is the EPA Project Officer (see below).
     The  complete report,  entitled "Investigation of Parasites in Sludges and
      Disinfection Techniques,"(OrderNo. PB86-135407'/AS; Cost:$22.95, subject
      to change) will be available only from:
           National Technical Information Service
           5285 Port Royal Road
           Springfield, VA22161
            Telephone: 703-487-4650
     The EPA Project Officer can be contacted at:
           Health Effects Research Laboratory
           U.S. Environmental Protection Agency
           Research Triangle Park, NC 27711
United States
Environmental Protection
Agency
Center for Environmental Research
Information
Cincinnati OH 45268
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