reporting on the implementation of the nitrate directive in hungary - ministry of environment and...
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Reporting on the implementation
of the Nitrate Directive in Hungary
dr. Lszl Balshzy
Ministry for Environment and Water
18-19 07 2007 Bucharest
mailto:[email protected]:[email protected] -
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Reporting is needed because
Commission has to supervise the national
implementation
Commission is obliged to report regularly
on the implementation of this Directive in
the EU to the Council and EP
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Art. 10(1) MS. shall submit a report to the Commission
containing the information outlined in AnnexV in each subsequent four-year period
(2) The Report shall be submitted within sixmonths of the end of the period
Deadline of the last reporting was: June 2004
Commission prepared a summary report on EU15 (available on CIRCA)
Next deadline: June 2008 (for 15), (Oct. 2008 (for10))
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Annex V
Information to be contained in reports1. Statement of the preventive actions
2. Maps of waters and NVZs
3. Monitoring system and results, designation(modifications) of NVZs
4. Summary of the Action Program
Remark: Almost all information is required about thetransposition and implementation of all relevantprovisions of Directive
No information about forms and details
Consequence: EU guidelines about the details to makenational reports quasi homogenous
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EU Guide 2000 I
Contents of the Guide
Additional information required in 1st report
Water quality assessment and maps
Designation (revision) of NVZs
Code of GAP Measures applied in AP
Evaluation of implementation of AP
Forecast on water (body) quality
Annexes (e.g. list of pieces of nationallegislation)
Remark: Guide contains formats of tables, maps
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EU Guide 2000 II
The Guide contains the format of required tables,
figures and maps (1: 1 000 000 or 1: 250 000)
Location of monitoring points: NUTS codes (Country
NUTS region Nr. station type code), coordinates
Mean and maximum values
Analysis of trends (comparison of data of this periodwith data of the earlier period) and indication of
points, which show increasing/decreasing trends
Strong increase/decrease: >5 mg/l or
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Development, promotion and implementation of code of GAP, Guide
Figures on agriculture and Nitrogen discharges
Information on elements of code of GAP
introduced or modified
Estimation of the percentage of farmers whovoluntarily apply the code
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Principal measures applied in the AP and implementation
Figures about number of animals and manureexcreated by them
Figures on chemical fertilisation (N, P)
Figures on other sources of N (P) inputs
Figures about N (P) balance
Information about elements of GAP
Figures about survelliance of different elements of
GAP Main points of difficulty in the implementation
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Forecast on water body quality and legal memorandum
Estimation on timetable for recovery of polluted
waters (numeric or cartographic format is
required)
Detailed information about legal transposition - TOC
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Messages (what we have learned) I
To start the preparation much earlier then youthink it would be enough
To start the systematic data collection at least4 years earlier than the reporting deadline
(e.g. in 2008 considering reporting in 2012) Systematic cooperation between
environmental, water and agriculturaladministration is needed from the early start
Designation/supervision/amendment of NVZsmay also have direct and indirect impacts onagricultural policies (e.g. subsidies, cross-compliance etc.)
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Messages (what we have learned) II
Comparison of the results of evaluation of the
status of waters by the ND and WFD is notrequired but may be useful
(e.g. area of NVZs and areas of water bodiesbeing at risk because of nutrient pollution)
The reasons of the differences can highlightsome weakness of monitoring or statusassessment
The preparation of RBMP is a good possibilityto supervise and harmonize these approaches
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Messages (what we have learned) III
Not enough to monitor the large rivers and their
relatively large tributaries as well as important lakes,
Representative monitoring network is needed for
small rivers/lakes too.
Representative monitoring is needed for gw. NO3 concentration of gw. depends at a large extent on
depth of well and the type of landuse (see next slides)
Gw. monitoring is a combined network: separate
monitoring wells, springs, operational wells; Monitoring sites hardly influenced by local pollution
sources.
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First HU Report (2000-2003)
Overview on legal and institutional frame of
transposition and implementation of ND
HU transposed ND by a Gov. Decree.
The water monitoring and evaluation of status as
well as designation of NVZs belong to MoEW.
Monitoring of soil and implementation of GAP
belong to MARD
Launched: education, leaflets issued, expert
advisory system
Remark: Commission required to modify the
legislation and some elements of the AP
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First HU Report (2000-2003) Water monitoring in HU
Monitoring of surface waters at > 3oo points
(1/300km2)
Monitoring of ground waters at > 1800 points
(1/50 km2)
Frequency of monitoring in every year:
surface waters: 1 per month (in general)
ground waters: 1-2 measurements per year
After supervision of the monitoring the network has
been changed
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Mean values of nitrate in surface waters 2000-2002
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Maximum nitrate concentration of surface waters 2000-2002
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First HU Report (2000-2003): Water quality assessment and maps II
Eutrofication
(Work is still going on to get a uniform classificationsystem in EU)
HU peresented figures on nitrate and a-chlorophyll,
phosphorus total, ortho-phosphate The proposed classification system (the quality grade
thresholds) seemed to be very strict and not adequate
to Central European natural conditions but we used
them
Not N, but P is the main driving force of
eutrophication in HU
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Mean values of nitrate concentration in groundwaters 2000-2002
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Changes in mean values of nitrate concentration between previous and last
reporting period
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0%
20%
40%
60%
80%
100%
Frequency of nitrate content of 18 740 groundwater wells and springs
aggregated acc. to the proposal of EU Guide
Compiled by J. Dek
50 mg/l 0,39963111 4,148351648 19,28089365
captive phreatic deep phreatic shallow
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Nitrate concentrations in groundwaters depending on depth and land use
compiled by J. Dek
100
m
forest
pasture
arable
orchard
settlement
0
20
40
60
80
100
meanNitrateco
ntent[mg/l]
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First HU Report (2000-2003): Designation (revision) of NVZs
HU designated NVZs
Recharge area of large shallow lakes and reservoirsused for public water supply
Open karstic areas and areas, where karstic aquifersare near the surface
Areas, where porous aquifers are near to the surface
Areas of hydrogeologic protection zones of wellfields
All areas, where nitrate content is near or over 50mg/l.
Remark: Commission required to supervise and enlarge
the designated areas a bit. Meantime Hungarychanged the philosophy a bit: NVZs have beendesignated at parcel level since Spring time of 2007.NVZs in HU: ~ 50% of the country, see next slide
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NVZs in Hungary separated by criteria
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NVZs as modified in 2007
Nit t i l f il (0 30 ) 2002
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Nitrate in upper layer of soils (0-30 cm) 2002
by P. Marth
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Animal Units
Animals 1000 Animal Units AU/1 ha of
agricultural land
1989 2004 1989 2004
Cattle 1279,2 578,4
Sheep 147,7 99,7
Pig 873,1 462,7
Poultry 208,3 131,3
Horse 60 53,6
Total 2568,3 1325,7 0,396 0,2226
Calculated agronomic NPK
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Calculated agronomic NPK
balances 1999-2003
1999 2000 2001 2002 2003
N 6 14 0 16 18
P -13 -8 -10 -5 1
K -13 -8 -12 -4 -6
Source: Research Institute for Soil Science and Agricultural Chemistry
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Prospects 1. scenario
traditional way of reporting
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Prospects II New way of reporting
After 2010 the reporting will be merged toWISE system
WISE has been developed for reporting onWFD as first step,
Next years reporting on other water relatedDirectives will be done by WISE
More formulated (templates, shape files)electronic reports are needed than earlier
To fulfil these requirements: electronic databanks are needed at local/regional/state andnational level
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Thank You for Your Attention!