2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
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Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />
P04 NITROGEN IN bREEDING LAyING hENS AND<br />
ENVIRONMENT PROTECTION<br />
MáRIA AnGELOVIČOVá, MAREK AnGELOVIČ and<br />
MIROSLAVA KAČánIOVá<br />
Faculty of Biotechnology and Food Sciences, Slovak University<br />
of Agriculture, Tr. A.Hlinku 2, Nitra, 949 76 Slovakia,<br />
maria.angelovicova@uniag.sk<br />
Introduction<br />
At EU–15 level the gross nitrogen balance in 2000<br />
was calculated to be 55 kg ha –1 , which is 16 % lower than<br />
the balance estimate in 1990, which was 66 kg ha –1 . In 2000<br />
the gross nitrogen balance ranged from 37 kg ha –1 (Italy)<br />
to 226 kg ha –1 (the netherlands). All national gross nitrogen<br />
balances show a decline in estimates of the gross nitrogen<br />
balance (kg ha –1 ) between 1990 and 2000, apart from<br />
Ireland (22% increase) and Spain (47% increase). The following<br />
Member States showed organic fertilizer application<br />
rates greater than the threshold of 170 kg ha –1 specified by<br />
the nitrates Directive in 2000: the netherlands (206 kg ha –1 )<br />
and Belgium (204 kg ha –1 ). The general decline in nitrogen<br />
balance surpluses is due to a small decrease in nitrogen input<br />
rates (–1.0 %) and a significant increase in nitrogen output<br />
rates (10 %). The gross nutrient balance for nitrogen provides<br />
an indication of potential water pollution and identifies<br />
those agricultural areas and systems with very high nitrogen<br />
loadings. As the indicator integrates the most important agricultural<br />
parameters with regard to potential nitrogen surplus<br />
it is currently the best available approximation of agricultural<br />
pressures on water quality. High nutrient balances exert pressures<br />
on the environment in terms of an increased risk of leaching<br />
of nitrates to groundwater. The application of mineral<br />
and organic fertilizers can also lead to emissions to the atmosphere<br />
in the form of nitrous dioxide and ammonia, respectively.<br />
Gross nitrogen balances are above 100 kg per ha in the<br />
netherlands, Belgium, Luxembourg and Germany. They are<br />
particularly low in most Mediterranean countries given the<br />
overall lower livestock production in this part of Europe.<br />
It is currently not possible to provide gross nitrogen balance<br />
estimates for the new EU Member States and the accession<br />
as the relevant statistical data are under elaboration. national<br />
balances, however, can mask important regional differences<br />
in the gross nutrient balance that determine actual nitrogen<br />
leaching risk at regional or local level. Individual Member<br />
States can thus have acceptable gross nitrogen balances at<br />
national level but still experience significant nitrogen leaching<br />
in certain regions, for example in areas with high livestock<br />
concentrations. There are a number of regions where pig<br />
livestock units have increased by more than 25 % between<br />
1990 and 2000 (for example, north-western Denmark, northwestern<br />
France, north-eastern Spain and northern Belgium).<br />
These are likely to be regional ‘hotspots’ for high gross nitrogen<br />
balances that can lead to environmental pressures. Member<br />
States with high nitrogen balances are making efforts<br />
to reduce these pressures on the environment. These build<br />
s341<br />
on a range of different policy instruments, requiring considerable<br />
political effort to succeed given the significant social<br />
and economic consequences of reducing livestock production<br />
in many affected areas 3,4 .<br />
Experimental<br />
We realized experiments with laying hens Shaver<br />
Starcross 288, which ingested feed mixture with different<br />
protein content. In six experiments laying hens fed feed<br />
mixture with protein contents 173.10 g per kilogram and in<br />
four experiments were used feed mixture with protein contents<br />
146.12 or 146.68 g per kilogram. It is soya cereal type<br />
assigned for laying hens. The laying hens ingested fodder ad<br />
libitum.<br />
Within experiments were researched:<br />
protein contents in feed mixture in one kilogram (chemical<br />
analysis – Kjeldahl method and calculation),<br />
excreted nitrogen [g kg –1 •<br />
•<br />
] in dropping per bird and day<br />
(chemical analysis – Kjeldahl method and calculation).<br />
Results<br />
Higher protein contents 173.10 g per kilogram of feed<br />
mixture resulted in excreted dropping at laying hens higher<br />
nitrogen contents in compare with protein contents 146.40 g<br />
per kilogram feed mixture. After ingestion of feed mixture<br />
with protein content 173.10 g per kilogram was nitrogen<br />
content in dropping from 1.88 g per bird and day. The laying<br />
hens, which fed feed mixture with protein contents 146.40 g<br />
per kilogram, excreted the nitrogen in dropping 1.38 g per<br />
bird and day. From these results follows that near decrease<br />
protein contents in feed mixture from 173.10 to 146.40 g<br />
per kilogram is possibility of nitrogen decrease in excreted<br />
dropping at laying hens about 26.60 % per bird and day. This<br />
different of decrease of excreted nitrogen in dropping at layers<br />
is statistically significant (P < 0.001). Correlation coefficient<br />
between content of crude protein in feed mixture and content<br />
of nitrogen in dropping at layers has high level r = 0.99.<br />
Low-protein diet system for layers with addition of<br />
amino acids is beside biologically-cattle-breeding, economical<br />
and ecological too.<br />
Progressive decrease of proteins content to 146.0 g per<br />
1 kg feeding mixture set up the order of limiting amino acids<br />
for layers: methionine, lysine, tryptophane and threonine 5 .<br />
On bases of results model trials on layers were concluded<br />
that feeding, fat-enriched mixture supplied DL-methionine,<br />
choline chloride and vitamin B 2 by need of the effective<br />
Table I<br />
Excreted nitrogen [g kg –1 ] in dropping at laying hens, which<br />
ingestion of feed mixture with different protein contents<br />
Trial Index SD v % t-test<br />
1 st CP [g kg –1 ] 173.10 0.91 0.52 55.68 +++<br />
2 nd CP [g kg –1 ] 146.40 0.32 <strong>2.</strong>68<br />
1 st n [bird day –1 ] 1.88 0.005 0.22 18.52 +++<br />
2 nd n[bird day –1 ] 1.38 0.02 1.57