************************************************************
75.  Emissions of nitrogen oxide gases during aerobic treatment
of animal slurries.
Burton, C. H.; Sneath, R. W.; Farrent, J. W. 

Bioresour-technol. Barking, Essex, England : Elsevier Applied
Science ; New York, NY : Elsevier Science Publishing Co., 1991-.
1993.  v. 45 (3) p. 233-235. 
Includes references.
Descriptor: pig-slurry; aerobic-treatment; emission-;
nitrogen-oxides
Abstract: Quantities of nitrous oxide, N2O, an important
greenhouse gas, were found in the effluent gases from controlled
continuous aerobic  treatment of pig slurry. Where
nitrifying-denitrifying conditions were encouraged (4-day
treatment time and aeration to a redox potential of -50  mV
Ecal), concentrations of this gas at times exceeded 1500 ppm and
accounted for 19% of the nitrogen lost from the slurry. Smaller 
concentrations of the gas (170 ppm) were found during short
treatments (1.5 days) where nitrifying activity would not be
expected; partial  nitrification is a possible explanation.
Quantities of nitric oxide (NO) (up to 100 ppm), and even small
amounts of NO2, were also found,  suggesting these previously
unquantified nitrogen transformation routes in the traditional
nitrogen cycle exist in aerobic treatment processes.
NAL Call No.: TD930.A32
************************************************************
76.  Enterobacterial and viral decay experimental models for
anaerobic digestion of piggery waste.
Mateu, A.; Mata Alvarez, J.; Pares, R. 

Appl-Microbiol-Biotech v.38, p.291-296. (1992).
Includes references.
Descriptor: pig-manure; piggery-effluent; anaerobic-digestion;
fecal-coliforms; bacteriophages-; survival-; ammonia-;
volatile-fatty-acids; inactivation-; models-; comparisons-;
coliphages-; lagoon-stabilization; cell-free-synthetic-media
Abstract: A laboratory study was conducted to determine the
effects of the continuous mesophilic anaerobic digestion of raw
pig manure in two  types of enteropathogenic microorganisms,
bacterial and viral. Faecal coliforms (indigenous to pig manure)
and coliphage f2 (ATCC 15766 B1)  were used as a model for some
indigenous enteropathogenic microorganisms. The study was
completed with laboratory survival experiments in  lagoon
stabilization of raw pig manure, for both models. Experiments for
f2 survival in cell-free synthetic medium were also carried out.
The  results show that the anaerobic digestion process is more
effective in eliminating viral than bacterial particles. Some
parameters related to the  ultimate biogas yield and kinetics
were also determined. Lagoon stabilization of raw pig manure
provides a more suitable environment for the  removal of faecal
coliforms than does anaerobic digestion. Finally, it was
concluded that volatile fatty acids appeared to be responsible
for the  elimination of faecal coliforms. The agent that causes
f2 inactivation is not well identified, although in some cases it
could be NH3 that seems  to act as a viricidal agent.
NAL Call No.: QR1.E9
************************************************************
77.  Equipment for application of animal slurry in field
experiments.
Petersen, J. 

J-agric-eng-res v.59, p.97-109. (1994).
Includes references.
Descriptor: slurry-spreaders; cattle-slurry; pig-slurry;
experimental-equipment; experimental-plots; band-placement;
soil-injection; slurry-pumps
NAL Call No.: 58.8-J82
************************************************************
78.  Estimated seepage losses from established swine waste
lagoons in the lower coastal plain of North Carolina.
Huffman, R. L.; Westerman, P. W. 

Trans-ASAE v.38, p.449-453. (1995).
Includes references.
Descriptor: pigs-; lagoons-; waste-water; seepage-;
coastal-plains; groundwater-; water-pollution; north-carolina
Abstract: Eleven well-established, swine waste lagoon systems in
the lower coastal plain of North Carolina were examined for
evidence of seepage  losses to the superficial aquifer. The sites
were selected to represent three major soil systems in the areas
of North Carolina with the highest  swine populations. Elevated
ammonium concentration was the strongest indicator of seepage.
Estimated seepage losses were small on 45% of  the systems
studied. On the remaining sites, estimates of total nitrogen
export indicated moderate to severe seepage losses. Several of
these  were near surface waters that probably served as discharge
points, minimizing the likelihood of extensive impact on
groundwater quality. No  assessment was made of effect on the
receiving surface waters. There was no apparent relationship
between seepage loss rates and major soil  system or style of
construction. Rather, the dominant factor appeared to be the soil
materials used in construction.
NAL Call No.: 290.9-Am32T
************************************************************
79.  Estimating lagoon size for swine waste management.
Nordstedt, R. A.; Baldwin, L. B. 

Agric-Eng-Fact-Sheet-Fla-Coop-Ext-Serv. Gainesville, Fla. : The
Service. 1990. (75) 2 p. 
Descriptor: pig-manure; waste-disposal; lagoons-; size-; volume-;
estimation-; florida-
NAL Call No.: S671.A38
************************************************************
80.  Evaluation of denitrification losses by the acetylene
inhibition technique in a permanent ryegrass field (Lolium
perenne L.) fertilized with  animal slurry or ammonium nitrate.
Schwarz, J.; Kapp, M.; Benckiser, G.; Ottow, J. C. G. 

Biol-fertil-soils v.18, p.327-333. (1994).
Includes references.
Descriptor: cattle-slurry; pig-slurry; mixtures-;
ammonium-nitrate; denitrification-; dicyandiamide-;
losses-from-soil; ammonium-nitrogen; nitrate- nitrogen;
soil-water-content; soil-temperature; lolium-perenne;
permanent-grasslands
NAL Call No.: QH84.8.B46
************************************************************
81.  Evaluation of overland flow treatment for swine lagoon
effluent.
Hawkins, G. L.; Hill, D. T.; Rochester, E. W.; Wood, C. W. 

Trans-ASAE v.38, p.397-402. (1995).
Includes references.
Descriptor: pigs-; lagoons-; effluents-; waste-water-treatment;
overland-flow; application-to-land; slopes-; runoff-;
percolation-; leaching-; usa-
Abstract: Overland flow, on slopes of 5 and 11%, was used as a
means of treating wastewater effluent from the second cell of a
swine waste  anaerobic lagoon system. Wastewater samples from
both surface runoff and soil percolate (depths of 0.3, 0.9, and
1.5 m) were collected and  analyzed for TKN-N, NH4-N, ON-N,
NO3-N, pH, COD, K, EC, and TP-P. Using these data, along with the
hydraulic loading rates and  quantitative runoff collection, mass
balances on the above parameters were calculated to determine the
surface treatment of the lagoon effluent.  These mass balances
suggest that overland flow is an excellent treatment system for
liquid lagoon effluents with mass reductions of greater than  60%
for all parameters on both slopes, except NO3-N, which had an
approximate increase of 1.7 times on the 11% slope. Samples
collected  from the three lysimeter depths (soil percolate)
suggest that NO3-N leaching from the plots may be a concern over
an extended period of use.  The runoff from overland flow systems
of this type will require further treatment.
NAL Call No.: 290.9-Am32T
************************************************************
82.  The evaluation of sawdust swine waste compost on the soil
ecosystem, pollution and vegetable production.
Kao, M. M. 

Water-Sci-Technol-J-Int-Assoc-Water-Pollut-Res-Control v.27,
p.123-131. (1993).
In the series analytic: Appropriate waste management technologies
/ edited by G. Ho and K. Mathew. Proceedings of the International 
Conference, held November 27-28, 1991, Perth, Australia.
Descriptor: composts-; pig-slurry; sawdust-; mixtures-;
soil-pollution; zinc-; copper-; brassica-pekinensis; crop-yield;
taiwan-
NAL Call No.: TD420.A1P7
************************************************************
83.  Evaluation of swine waste composting in vertical reactors.
Lau, A. K.; Liao, P. H.; Lo, K. V. 

J-Environ-Sci-Health-Part-A-Environ-Sci-Eng v.A28, p.761-777.
(1993).
Includes references.
Descriptor: pig-manure; pig-slurry; composting-; waste-treatment;
moisture-content; height-; temperature-;
particle-size-distribution; shrinkage-; compaction-;
statis-pile-system
NAL Call No.: TD172.J6
************************************************************
84.  Evaluation of the stabilization level of pig organic waste:
influence of humic-like compounds.
Govi, M.; Ciavatta, C.; Sitti, L.; Gessa, C. 

Commun-soil-sci-plant-anal v.26, p.425-439. (1995).
Includes references.
Descriptor: pig-slurry; sludges-; pig-manure; straw-;
composting-; composts-; maturation-; decomposition-;
humification-; humic-acids; fulvic-acids; organic-matter;
isoelectric-focusing; degradation-; degree-of-humification
NAL Call No.: S590.C63
************************************************************
85.  Evaluation of various flocculants for the recovery of algal
biomass grown on pig-waste.
Buelna, G.; Bhattarai, K. K.; De La Noue, J.; Taiganides, E. P. 

Biol-Wastes v.31, p.211-222. (1990).
Includes references.
Descriptor: pig-farming; wastes-; biological-treatment;
chlorella-; ponds-; biomass-production; flocculants-;
sedimentation-; singapore-
NAL Call No.: TD930.A32
************************************************************
86.  Exogenous isolation of mobilizing plasmids from polluted
soils and sludges.
Top, E.; Smet, I. de.; Verstraete, W.; Dijkmans, R.; Mergeay, M. 

Appl-environ-microbiol v.60, p.831-839. (1994).
Includes references.
Descriptor: polluted-soils; activated-sludge; plasmids-;
genetic-transformation; escherichia-coli; alcaligenes-;
gene-transfer; mating-; agricultural-soils; pig-manure;
sandy-loam-soils; conjugative-plasmids; alcaligenes-eutrophus;
conjugation-
Abstract: Exogenous plasmid isolation was used to assess the
presence of mobilizing plasmids in several soils and activated
sludges.  Triparental  matings were performed with Escherichia
coli (a member of the gamma subgroup of the Proteobacteria) as
the donor of an IncQ plasmid  (pMOL155, containing the heavy
metal resistance genes czc: Co(r), Zn(r), and Cd(r)), Alcaligenes
eutrophus (a member of the beta subgroup of  the Proteobacteria)
as the recipient, and indigenous microorganisms from soil and
sludge samples as helper strains.  We developed an assay to 
assess the plasmid mobilization potential of a soil ecosystem on
the basis of the number of transconjugants obtained after
exogenous isolations.  After inoculation into soil of several
concentrations of a helper strain (E. coli CM120 harboring IncP
[IncP1] mobilizing plasmid RP4), the log  numbers of
transconjugants obtained from exogenous isolations with different
soil samples were a linear function of the log numbers of helper 
strain CM120(RP4) present in the soils.  Four soils were analyzed
for the presence of mobilizing elements, and mobilizing plasmids
were  isolated from two of these soils.  Several sludge samples
from different wastewater treatment plants yielded much higher
numbers of  transconjugants than the soil samples, indicating
that higher numbers of mobilizing strains were present.  The
mobilizing plasmids isolated from  Gent-O sludge and one plasmid
isolated from Eislingen soil hybridized to the repP probe,
whereas the plasmids isolated from Essen soil did not  hybridize
to a large number of rep probes (repFIC, repHI1, repHI2, repL/M,
repN, repP, repT, repU, repW, repX).  This indicates that in
Essen  soil, broad-host-range mobilizing.
NAL Call No.: 448.3-Ap5
************************************************************
87.  Fate of biological and chemical contaminants from on-site
disposal of liquid piggery wastes: results from a soil column
study.
Lam, K. C.; Ng, S. L.; Neller, R. J. 

Water-Sci-Technol-J-Int-Assoc-Water-Pollut-Res-Control v.27,
p.63-75. (1993).
In the series analytic: Appropriate waste management technologies
/ edited by G. Ho and K. Mathew. Proceedings of the International 
Conference, held November 27-28, 1991, Perth, Australia.
Descriptor: pig-housing; waste-disposal-sites; liquid-wastes;
application-to-land; hong-kong
NAL Call No.: TD420.A1P7
************************************************************
88.  The fate of nitrogen from 15N-labeled straw and green manure
in soil-crop-domestic animal systems.
He, D. Y.; Liao, X. L.; Xing, T. X.; Zhou, W. J.; Fang, Y. J.;
He, L. H. 

Soil-sci v.158, p.65-73. (1994).
Includes references.
Descriptor: oryza-sativa; paddy-soils; pigs-; goats-; rice-straw;
green-manures; application-to-land; feeds-; animal-manures;
nitrogen-; recovery-; nutrient-availability; nitrogen-cycle
NAL Call No.: 56.8-So3
************************************************************
89.  Fate of residuals in nitrification-denitrification treatment
of piggery wastewaters.
Germirli, F.; Bortone, G.; Orhon, D.; Tilche, A. 

Bioresour-technol. Barking, Essex, England : Elsevier Applied
Science ; New York, NY : Elsevier Science Publishing Co., 1991-.
1993.  v. 45 (3) p. 205-211. 
Includes references.
Descriptor: piggery-effluent; nitrification-; denitrification-;
waste-water-treatment; chemical-oxygen-demand; italy-;
sequencing-batch-reactor
Abstract: A careful appraisal of piggery wastewaters should be
made mainly because of their high content of organic constituents
together with the  nitrogen and stringent effluent limitations
involved. Specific emphasis should be given to the COD of the
wastewater as it contains, aside from a  biodegradable portion, a
residual fraction which persists throughout the treatment
process. Experimental evaluations indicated that the effluent  of
a laboratory-scale SBR contained significant amounts of
non-biodegradable COD. Since SBR was primarily operated to
achieve nitrification- denitrification, a method previously
developed for the assessment of the influent soluble inert COD,
S(I) was modified in a way to reflect the  possible impact of the
nitrification and denitrification processes. The paper also
summarizes the performance of SBR with respect to its nitrogen 
removal potential from piggery wastewaters.
NAL Call No.: TD930.A32
************************************************************
90.  Feedlot runoff control--demonstration site: swine and beef
lot--Location: Delaware County.
AE. Ames, Iowa : Cooperative Extension Service, Iowa State U
niversity. Nov 1993. (3077h) 2 p. 
Descriptor: pigs-; beef-cattle; feedlots-; runoff-;
feedlot-wastes; waste-disposal
NAL Call No.: S671.A22
************************************************************
91.  Feedlot runoff control--Demonstration site: swine
lot--location: Pocahontas County.
AE. Ames, Iowa : Cooperative Extension Service, Iowa State U
niversity. Dec 1993. (3077k) 2 p. 
Descriptor: pigs-; feedlots-; feedlot-wastes; runoff-;
waste-disposal
NAL Call No.: S671.A22
************************************************************
92.  Feedlot runoff control--demonstration site: swine
lot--Marshall County.
Lorimor, J. 

AE. Ames, Iowa : Cooperative Extension Service, Iowa State U
niversity. Sept 1993. (3077f) 2 p. 
Descriptor: pigs-; feedlots-; feedlot-effluent; feedlot-wastes;
demonstration-farms
NAL Call No.: S671.A22
************************************************************
93.  Feedlot runoff control demonstration site: swine
lot--Pottawattamie County.
Lorimor, J. 

AE. Ames, Iowa : Cooperative Extension Service, Iowa State
University. Feb 1994. (3077n) 2 p. 
Descriptor: pig-farming; feedlot-wastes; runoff-;
farm-management; demonstration-farms; iowa-
NAL Call No.: S671.A22
************************************************************
94.  Feedlot runoff control--demonstration site: swine
lot--Washington County.
AE. Ames, Iowa : Cooperative Extension Service, Iowa State U
niversity. Sept 1993. (3077e) 2 p. 
Descriptor: pigs-; feedlots-; feedlot-effluent; feedlot-wastes;
waste-disposal; demonstration-farms
NAL Call No.: S671.A22
************************************************************
95.  The fertilizer value of agricultural manure: simple rapid
methods of assessment.
Piccinini, S.; Bortone, G. 

J-Agric-Eng-Res v.49, p.197-208. (1991).
Includes references.
Descriptor: pig-manure; dairy-cattle; cattle-manure;
chemical-analysis; analytical-methods; equations-; accuracy-;
instruments-; italy-
Abstract: This paper presents the results of a series of
analytical tests performed on pig and dairy cattle manure in
order to establish the extent of  the correlation between: dry
matter (TS) and specific gravity (SG); TS and total Kjeldhal
nitrogen (TKN) and total phosphorus (Pt); SG and  TKN and Pt. In
addition, two N-meters for field use were also used to estimate
the ammonium (NH4-H) content. All the variables (TS, SG,  TKN,
Pt, NH4-N) show a high index of correlation for both the pig and
dairy cattle slurry and the linear relations applied proved
adequate in all  cases. Though the precision of the equations is
not very high, the estimate for TKN and Pt content, obtained from
the relationship between the  SG and these elements is
nevertheless acceptable for practical farm use of animal manure.
NAL Call No.: 58.8-J82
************************************************************
96.  Iowa State University. Cooperative Extension Service. First
steps : moving toward sustainability : livestock management
(hogs).  First steps; moving toward sustainability. [Ames, Iowa?]
: Extension, [1990?] 1 videocassette (28 min.) : sd., col..
"Program was prepared with the support of USDA Agreement
88-COOP-1-3523.".
Presents three hog producers who have made changes in their
production methods, based on sustainable agricultural decisions
involving  productivity, high volume, and environmental concerns
and effects. The changes range from a totally pasture farrowing
and finishing process to  a drug-free finishing process to having
hogs pastured on a corn stubble field to provide manure to the
field while they feed off the corn stubble  and fallen cobs.
Videocassette-no.1234.
Swine-/ Swine-farrowing-facilities/ Manure-handling/
Sustainable-agriculture.
************************************************************
97.  Flat bottom gravity drain gutters for swine manure.
Meyer, V. M. 

PM-Iowa-State-Univ-Coop-Ext-Serv. Ames, Iowa : Iowa State
University, Cooperative Extension Service. Aug 1992. (1377,rev.)
4 p. 
Descriptor: pig-manure; pig-housing; piggery-effluent;
drainage-systems; design-
NAL Call No.: 275.29-IO9PA
************************************************************
98.  Flooring for swine.
Harmon, J. D.; Muehling, A. J. 

Pork industry handbook -- p.1-6. (1993).
Descriptor: pigs-; floors-; floor-type; defecation-; pig-housing;
feet-; lesions-; sanitation-; pig-manure
NAL Call No.: SF395.P62
************************************************************
99.  Fly control on swine.
Williams, R. E. 

E-Purdue-Univ-Coop-Ext-Serv. West Lafayette, Ind. : The Service.
July 1992. (9,rev.) 2 p. 
In subseries: Livestock Insects.
Descriptor: diptera-; pigs-; insect-control; insecticides-;
spraying-; ovicides-and-larvicides; pig-manure
NAL Call No.: SB844.I6P8
************************************************************
100.    Free and immobilized cultures of Spirulina maxima for
swine waste treatment.
Canizares, R. D.; Dominguez, A. R.; Rivas, L.; Montes, M. C.;
Travieso, L.; Benitez, F. 

Biotechnol-Lett v.15, p.321-326. (1993).
Includes references.
Descriptor: spirulina-; pigs-; excreta-; biological-treatment;
immobilization-; ammonium-nitrogen
Abstract: We have analyzed the behavior of Spirulina maxima at
increasing concentration of ammonium nitrogen present in swine
waste when it is  either growing in suspension or immobilized in
polymeric supports. We compared the response of Spirulina maxima
growth to different  concentrations of aeration stabilized swine
waste (total phosphorus, ammonium nitrogen) as a way to determine
the treatment efficiency of both  systems. At a dilution of 50%
of swine waste, the suspended system reached the best results for
biomass concentration and nutrient removal. In  the immobilized
system at dilutions of 25 and 50% of swine waste, more than 90%
ammonium nitrogen removal was obtained, and the optimal  cell
concentration for immobilization was 2 g/l (wet basis).
NAL Call No.: QR53.B56
************************************************************


monday tuesday wednesday thursday friday saturday sunday partyday funday niceday 53A2.2583 53A4.2584 53A5.2585 53A6.2586 53A6.2587 53A8.2588 53A9.2589 53A9.259A 53AA.258A 5412.2692 5413.2693 5414.2694 5415.2695 5415.2696 5417.2697 5418.2698 5419.2699 5421.27A1 5422.27A2 5422.27A3 5424.27A3 5424.27A5 5424.27A6 5427.27A7 5428.27A8 5429.271A 5429.27A9 542A.27AA 5431.2711 5431.2712 5433.2713 5434.2714 5434.2715 5436.2715 5437.2717 5438.2718 5439.2719 5441.2721 5441.2722 5443.2723 5444.2724 5444.2725 5446.2726 5446.2727 5448.2728 5449.2729 5449.273A 544A.272A 5451.2731 5452.2731 5453.2733 5454.2733 5454.2735 5456.2736 5456.2737 5456.2738 5459.2739 5461.2741 5462.2742 5463.2743 5463.2744 5465.2745 5465.2746 5467.2747 5467.2748 5469.2749 546A.274A 5471.2751 5471.2752 5473.2753 5474.2753 5475.2755 5476.2756 5476.2757 5478.2758 5479.2759 547A.275A 5482.2762 5483.2762 5483.2764 5485.2765 5485.2766 5485.2767 5488.2767 5489.2769 5489.277A 548A.2761 548A.276A 5491.2771 5492.2772 5493.2773 5494.2774 5495.2775 5496.2776 5497.2777 5498.2778 5499.2779 54A1.2681 54A1.2682 54A1.2683 54A4.2684 54A5.2685 54A6.2686 54A6.2687 54A8.2688 54A8.2689 54A8.2691 54AA.268A 5512.2792 5512.2793 5514.2794 5514.2795 5516.2796 5517.2797 5517.2798 5519.2799 5522.28A2 5523.28A3 5524.28A4 5524.28A5 5524.28A6 5527.28A7 5527.28A8 5529.2811 5529.281A 5529.28A9 552A.28A1 552A.28AA 5532.2812 5532.2813 5534.2814 5535.2815 5536.2816 5536.2817 5538.2818 5539.2819 5542.2822 5542.2823 5544.2824 5545.2825 5546.2826 5546.2827 5548.2828 5549.2829 5549.283A 554A.2821 554A.282A 5551.2831 5552.2832 5552.2833 5554.2833 5555.2835 5555.2836 5557.2837 5557.2838 5559.2838 5559.284A 5561.2841 5562.2842 5563.2842 5563.2844 5563.2845 5566.2846 5567.2847 5568.2848 5568.2849 5571.2851 5571.2852 5573.2853 5574.2854 5575.2855 5575.2856 5575.2857 5578.2858 5579.2858 557A.285A 5581.2861 5582.2862 5582.2863 5584.2864 5585.2865 5586.2866 5586.2867 5586.2868 5589.2869 558A.286A 5591.2871 5592.2872 5593.2873 5594.2874 5595.2875 5596.2875 5597.2877 5598.2878 5598.2879 559A.287A 55A1.2781 55A1.2782 55A1.2783 55A4.2784 55A5.2785 55A6.2786 55A7.2787 55A8.2788 55A9.2788 55A9.2791 55A9.279A 55AA.278A 5611.2891 5612.2892 5613.2893 5613.2894 5613.2895 5616.2896 5617.2897 5621.29A1 5622.29A2 5623.29A3 5624.29A4 5624.29A5 5624.29A6 5627.29A7 5628.29A8 5628.29A9 562A.29AA 5631.2911 5632.2912 5632.2913 5634.2914 5635.2915 5635.2916 5637.2917 5637.2918 5639.2918 5639.2921 5639.292A 563A.291A 5642.2922 5643.2923 5643.2924 5645.2925 5646.2926 5646.2927 5648.2928 5649.2929 5652.2932 5652.2933 5654.2934 5654.2935 5654.2936 5654.2937 5658.2938 5659.2939 565A.2931 565A.293A 5661.2941 5662.2941 5663.2943 5664.2944 5665.2945 5666.2946 5666.2947 5666.2948 5669.2949 5669.295A 5671.2951 5672.2952 5673.2953 5674.2954 5675.2955 5676.2956 5677.2957 5678.2958 5678.2959 5681.2961 5682.2962 5683.2963 5684.2964 5685.2965 5685.2966 5687.2967 5688.2968 5689.2969 5689.2971 568A.296A 5692.2972 5693.2973 5693.2974 5695.2975 5696.2976 5697.2977 5698.2978 5699.2979 56A1.2881