1988 SHEEP MONITORING PROGRAMME JANUARY — DECEMBER 1988
P.A. Colgan & BJ. Scully
June 1989
Nuclear Energy Board, 3 Clonskeagh Square, Clonskeagh Road, Dublin 14. 1988 SHEEP MONITORING PROGRAMME JANUARY — DECEMBER 1988
P.A. Colgan & BJ. Scully
June 1989
Nuclear Energy Board, 3 Clonskeagh Square, Clonskeagh Road, Dublin 14. CONTENTS
i. i\ i Ronrcnox
2. UPLAND I-ARM MEASUREMEN I PROGRAMME. 2.1 Selection oi Areas for Monitoring 2.2 Siiiu'ture of (he Monitoring Programme 2.H Kqui])inent 2.1 Measurement I ec hniquc 2."> Results 2.(i Variation in Activity between Lambs and Hues 2.7 Comparison vviih Results from 1987
•*. STATISTICAL EVAL UATION OF UPLAND FARM RESULTS 3.1 Introduction 3.2 Statistical Testing •U Results 1. SLAUGHTERHOUSE MONITORING PROGRAMME 1.1 Description oi (he Programme •1.2 Results
5. LABORATORY ANALYSIS OF SHF.LPMF.AT FROM BUTCHERS' SHOPS
6. RADIATION DOSF.S TO CONSUMERS
7. CONCLUSIONS AND RECOMMENDATIONS
8 ACKNOWLEDGEMENTS
9. REFERENCES
GLOSSARY OF TERMS
APPENDICES
Tables
1. In Vivo Sheep Monitoring Programme — Farm Measurements
2. Percentage chance of clearing a flock with a specified proportion oi sheep above a pie-defined upper threshold for a sample size of 20 per flock
3. Percentage chance of clearing a flock with a specified proportion of sheep above a pre-defined upper threshold for a sample size of 100 per flock
4. Results of Slaughterhouse Monitoring. January — December 1988
5. Radiocaesium in Lamb Samples. January — December 1988
6 Radiation Doses to Members of the Public
Figures 1. Areas in which On-Farm Monitoring was undertaken 2. Distribution of Radiocaesium Activities in Sheep being received at Slaughterhouses ABSTRACT
An extensiw sheep monitoring programme hits been uinlcri;ikcn during 1988 In the Xu< leat Knergv Hoard in conjunction with the Departments of Agriculture and Food and of Health. This programme included the on-fann monitoring of mountain slice/), the regular monitoring at slaughterhouses serving both the domestic and c\poits markets, and the laboratory analysis of sheepmeat sold across the butcher's counter.
A major on-farm monitoring programme involved in vivo measurements of slice/) and lambs grazing on upland />asturcs in 17 counties, and was an extension of the previous work undertaken in tlie pcrioil October to December 1987.
A total of 12:18 farms were visited and 26.970 animals in all were monitored. Ol these. .)/.;.•; (I2.S"O) showed measured activities above 600 Becquerels /;<•/ kilo (B(j Kg), of which 1021 (3.8%) were above 1000 Bq Kg. The highest activities measured were in Counties Donegal. Sligo. Lei trim. Cavan and Waterford. A small number of individuals in excess of 1000 Bq Kg were also identified in Counties Mayo. Roscommon. Louth. Tipperary and Kerry. The highest individual measurement was just under 3,000 Bq
%•
In vivo monitoring was also undertaken at slaughterhouses serving both the domestic and export markets, (her 16,000 animals were measured during 1988 and 99.')% of these showed activities below 200 Bq Kg. Just I animals exceeded 600 Bq Kg and these w-. re returned to the farmers for lowland finishing.
Analysis of 223 samples of sheepmeat taken from butchers' shops showed a population weighted mean activi.y of 9.5 Bq kg, which at normal consumption rates corresponds to an annual effective dose equivalent of 0.0009 milliSievert, less than 0.1 % of the recommended dose limit for members of the public of 1 milliSievert.
The report concludes that the regular consumption of shee/mieat. even at the highest activity levels measured on some upland farms, does not constitute a significant radiological health hazard. The need for continued monitoring at slaughter outlets is highlighted and it is suggested that advice to tanners on the best means of reducing activity in slice/) should be available. Finally, the authors call for research on the behaviour of radionuclides in upland soils to be undertaken with a view to understanding the uptake and transfer of radioactivity in the affected areas. 1. INTRODUCTION
Following the ai c idem at the Chernobyl nui leal power station in Api il \'M(i, hca\ y rainfall ihrnughoui iicland dining llie peiiod '2.<> May I9HI). resulted in the deposition o( radionuc lides on heibagc jnd pasture. Klevaled levels ol radiocacsmm (caesium-137 ami caesium-13'1) were subsequently measuied in Irish soils (1.2).
Caesium is known lo bind to the (lay mineral fraction of soils, and where land is used foi tillage and pasture, the transfer of caesium into vegetation and agricultural produce has been shown lo be negligible 0).
Sue h is not always the case in upland areas. With poor-quality, piaty soils, (heir high organic content results in low binding of caesium, which is therefore more available for uptake by plants. Many of these upland soils are also deficient in potassium, which is chemically similar to caesium and, therefore, competes with il in the transfer raci hanism. The net! result is that there is enhanced uptake of caesium by upland plants, including grasses, moss and heather. Consequently, sheep whose diet contains a large percentage of such plants arc- likely lo sh'»w elevated levels of radioactivity in (heir flesh.
Since mountain sheep are normally finished on lowland pasture for a period of up to 12 weeks prior to slaughter, the biological half-life of radiocaesiutn in sheep of 10-12 days results in a rapid decrease in the radiocaesium concentration in the flesh. This means that by the time animals are presented for slaughter the activity level, even in those which may be uriaccepiably high while on upland grazing, is normally well within national and international standards.
A major on-farm monitoring programme of sheep was undertaken by the Board, in conjunction with officials of the Department of Agriculture and Food in the period October to December 1987 (J). This study identified 92 District Electoral Divisions (DEDs) in counties Donegal, Sligo, Leitrim, Mayo, Gal way and Waterford in need of further monitoring in 1988. In addition, it was decided that the 1988 programme should include upland areas in counties Carlow, Cavan, Clare, Cork, Kerry, Laois, Louth, Offaly, Roscommon, Tipperary and Wexford in order to compile a more comprehensive picture of the activity levels in mountain sheep throughout Ireland.
In order to protect further the consumer, in vivo monitoring of sheep has been undertaken at the main slaughterhouses dealing with both the home and export markets since January 1988. In addition, a number of smaller slaughterhouses killing primarily for the domestic market was regularly visited.
The Nuclear Energy Boaru jlso carries out national surveys to determine the activity levels in sheepmeat and other food products. Two surveys of the activity in sheepmeat sold across butchers' counters were undertaken during 1988 — the first took place in May and the second in October. These programmes were designed to confirm the results of slaughterhouse monitoring and lo ensure that sheepmeai as sold is suitable for human consumption.
This report summarises the work undertaken by the Board during 1988, and includes the icsi.lis of in invo farm measurements, slaughterhouse monitoring and butchers' shops surveys relating to sheep and sheepmeat. An interim report, dealing with the first 9 months of 1988, has already been published (5). That report has now been expanded to include the additional data from the last quarter of the year, as well as giving a more detailed discussion of (he results obtained. A new section dealing with statistics has also been included, and detailed resuhs and maps of the areas where monitoring on upland farms was undertaken have been appended to the text.
The on-farm measurements and slaughterhouse monitoring programmes were undertaken with the co-operation and assistance of officials and staff of the Department of Agriculture and Fowl, and .sheepmeai samples from butchers' shops were supplied by Environmental Health Officers from the Department of Health. The contribution of both Departments to the work described in this report is gratefully acknowledged. 2. UPLAND FARM MEASUREMENT PROGRAMME
2.1 Selection of Areas of Monitoring
Dining a three-month period at ihe end of 1987. llie /;; inn moniloiing of upland sheep took pla< <• in selected parts of ihe counties Donegal. Galway. Kilkenny. I.eiiriin. Mayo. Roscominon. Sligo and Waterford. Between I and "> farms in each ol the .'502 DKDs selec led were visited and <>i) ea< h (aim a total ol 10 animals, when- available, were moniloied. Statistical testing was then undeitaken m oldei to identify DKDs deemed (o be "rescued and "< leaied" in each ol the counties visited. "Cleared DKDs would tcc|iiire no lurthcr monitoring, while those designated as "reserved" would be- revisited itt 1988.
Besides revisiting the designated parts ol counties Donegal. I .ein ini. Mayo. Galway. Sligo and U'ateiloid as described above, il was decided to extend the scope of the- survey to include otbei upland aieas not previously monitored. The lollowing areas were therefore included in the- 1988 programme ol work:
1. The lowland peais and .Slieve Bloom Mountains in I.aois and Offaly. 2. The Blackstairs Mountains in Callow and Wexford. .'i. The Cooley Mountains in Lotah. 1. The Knockniealdown and (ialtec Mountains in Tipperary. f>. The Slieve Aughty Mountains in Clare. 6. The Curlew Mountains in Rosrommon. 7. The Iron Mountains and other upland areas in Cavan. 8. All upland areas in west Cork. 9. All upland areas in Kerry.
The areas in which in-vivo monitoring was undertaken are shown in Figure 1.
FIGURE 1 Areas in which On-Farm Monitoring was Undertaken
"•'' I'lic l'.W7 piogiammc ol wink had idcntilied (J2 Distiict l\lei ioi.il Dhisioiis (Dl-'.l)si in ncril ol huilxi monitoiing. In setting up tin- I!t88 piogiamme. il was decided to extend (he inoniioiing liosn JO animals on one iann in each DI-.I) lo include a niiniimim ol 20 animals on each oi Jive i'tius pel OKI). I here were ihiee reasons foi extruding the scope ol (he survey in ihis way: I. The statistical analysis oi (he M)H7 in vivi> inoniioiing results was designed to declare areas "reserved" if they could not be "cleaied". h was poinled out at thai (ime thai I'IIMIK'I sampling in areas deemed to be- "leseived" would be- needed belore any linn conclusions could be drawn. It was decided to extend ihe number of sheep monitored per DEO to 100 in order to improve (tie quality of subsequent statistical analysis. 1. The 1987 results had shown considerable variations in the radiocaesium concentrations in sheep from different farms within the same DFD. Measurements made on only one farm cannot provide an estimate oi the variation in activity throughout the DKD, and therefore one must question the validity of "clearing" an entire DEI) based solely cm one set of measurements. By selecting five farms within each DF.D a better picture tan be obtained of the variation in activity levels throughout its area. 3. One of the fundamental aspects of the statistical testing of the 1987 results was to confirm that the results from each farm followed a normal distribution. With a sample size of 10 animals, this was often difficult, and so an increase in the number of animals monitored on each farm was considered necessary in order to overcome this problem. It was recognised that not every farmer would be able to present the required number of animals for measurement, and that in some DEDs there would be less than 5 farms on which sheep grazed on heather. Where such circumstances could be identified in advance, an increased number of animals was monitored at other farms. In setting up the work programme, it was decided to measure 20 ewes and 5 lambs on each farm visited. Research work undertaken by the Ministry of Agriculture Fisheries and Food (MAFF) in the United Kingdom (6) had shown no consistent relationship between activity in animals and their age for animals greater than 12 weeks old. While the majority of mountain ewes are retained for breeding rather than slaughtered for human consumption, the activity measured in ewes would be typical of what one would expect in more mature lambs which normally go for slaughter when 6—8 months old. By including a number of young lambs in the study, one would also have some idea of the activity in younger animals which might be slaughtered at an earlier age. 2.3 Equipment All measurements were made using portable scintillation detectors. The specific models used were the John Caunt SN1A and the Ludlum 2220 with appropriate probe attachments. In the case of the Ludlum 2220, additional lead shielding was affixed to the sides of the detector in order to reduce the background count rate. The threshold and window of the single channel analyser were set to measure the caesium -137 and caesium -131 gamma peaks in the energy lange 600—800 keV. Kach piece of equipment was initially calibrated using a series of laboratory standards. Subsequently a number of animals, whose activity had previously been estimated by in vivo monitoring, were slaughtered anci analysed by high resolution gamma sixrirometry. This more detailed analysis gave similar results to those obtained by the in vivo technique, thereby confirming the assigned conversion factor for each instrument. 2.4 .Measurement Techni All measiilemcnts weir made using the in \i\<> let hni<|iie developed In MAM- (7). I-sseiiliallv ihis involves holding the piohc next l<> I lit" llesh\ pail of llle sheep's mm]) lot .1 specified penoii of (inn . and iisiiit; the molded numbei of counts, coiiec ted loi hat kgroiiud ladialion. to calc ula(<- the ac mm piesent in the animal. A full description of the techniques involved is published elsewhere (-1.7.8). 2.5 Results I he- piogianime o| work commenced on Monday Hith May 1988 on the lowland peats in Laois and Ofialy, and was extended lo all upland areas in late June and early July. The sheep breeding paiiern in Ireland is such that animals remain on lowland pasture after lambing and would only return to upland glazing during the month of May. It was previously shown (fj) thai the peak average ac livily in sheep will he leached 5 weeks aher consumption of contaminated herbage had commenced, and, so, an earliet start to the programme in upland areas would not have been fruitful. Dm ing the 22 weeks ol the- survey, I .'I'M farms were visited and a total of 26.97O animals were monitored. Of these, 3.155 (12.8".',) animals showed activities in excess of (iOO Bq kg. of which 1.021 (3.8%) were above 1,000 Hcj kg. Kleven (0.01%) animals exceeded 2.000 Bq kg. with the highest individual reading being just below 3,000 Bq kg. The results for each county are summarised in Table I. and a full listing of the results for each farm is given in Appendix I. These results were subsequently compiled by DKD and are reported in .Appendix II. Appendix III contains county maps showing DKDs in which animals were measured as having ratJiocaesium concentrations in excess of 2,000. 1 .500. 1.000 and 600 Bq kg. TABLE 1 In Vivo Sheep Moniloring Programme Farm Measurements County No. of Farms No. of sheep No. of animals above Range visited monitored 600 Bq kg 1,000 Bq/kg Bq/kg Carlow 18 3")fi 0 0 0- 109 Cavan (58 1372 325 ( 21%) 58 ( 1%) 0-1776 Clare 28 M9 1 ( The monitoring results for each county can be summarised as follows: DONEGAL The area identified for monitoring as a result of the 1987 work programme was concentrated in the north-west part of the county between Letterkenny, Doochary and Dunlewy, stretching southwards through Barnesmore Gap to Lough Derg. The DED of Glentogher, in the Inishowen peninsula, was also included. A total of 147 farms were visited, and 3610 individual animals in 32 DEDs were monitored. Of these, 1678 (47%) divided between 122 farms showed measured radiocaesium activities above 600 Bq/kg, of which 551 (15% of the total) were above 1000 Bq/kg. On 67 of the farms, an activity level of 1000 Bq/kg was exceeded in at least one monitored animal. In 10 of the 32 DEDs visited, animals were identified with radiocaesium activity in excess of 1500 Bq/kg, and four animals exceeded 2000 Bq/kg. Three of these were lambs, from the DEDs of Meencargagh and Cloghan; the fourth, a ewe, was from Creenasmear. . SLIGO Monitoring in Sligo was concentrated in the Ox Mountains, with a further 2 DEDs (Ballinashee and Shancough) on the border with Leitrim also being visited. Measurements were made on 64 farms in 14 DEDs, and a total of 1285 animals were monitored. 217 (17%) of animals divided between 32 farms showed radiocaesium activities above 600 Bq/kg, and 64 (5%) of these were above 1000 Bq/kg. The highest individual readings were in the DEDs of Breencorragh, Glendarragh and Templeboy South in the Ox mountains, and in Shancough in the Iron mountain range. On one of the farms in the Shancough DED, 19 of the 20 animals monitored were above 1000 Bq/kg, with 4 ewes and 1 lamb exceeding 1900 Bq/kg. LEITRIM The programme of work undertaken involved measurement of 1864 animals on 94 farms in 20 DEDs, all located in the northern half of the county. All of this area had previously been monitored in 1987, and 19 DEDs had been "reserved" at that time. A total of 391 (21%) animals showed radiocaesium activities above 600 Bq/kg, of which 73 (4% of the total) were above 1000 Bq/kg. The highest individual reading was in the DED of Cloonclare, where over 2,000 Bq/kg was recorded in a 4 month old lamb. On this particular farm, the flock had access to both grass and heather, and it is interesting to note that the other 21 animals monitored all showed levels of activity below 1000 Bq/kg. The DEDs adjacent to Shancough in Co. Sligo — Arigna, Drumahaire and Killanummery — showed activities up to 1500 Bq/kg, somewhat less than that recorded across the county border. CAVVN A iota) of 68 farms in II DEDs in the north-west pan of tin1 county between I.ciuim and Fermanagh was visited. In all U572 sheep were monitored, of which .325 (21%) were above (iOO Bq kg. Of lhe.se, 58 (1%) exceeded 1000 Bq kg, and these were divided between II farms in 9 DEDs. The highest irulividtial reading was 1776 Bq kg in (lie OKI) of Benbrack. ROSCOMMON A total of 12 farms located north-west of Boyle and adjacent to the county borders with Sligo and I.eitrim was visited. The highest activities were in the DEDs of Lough Allen and Altagowlan, where up to 1500 Bq kg were recorded in a total of 12 animals from 3 different farms. Similar activities were recorded in the neighbouring DEI) of St. Patricks in Co. Leitrim, MAYO Much of the west and north-west of Co. Mayo had been monitored during 1987, and 13 DEDs identified for further monitoring in 1988. The individual DEDs were well scattered, but included an area west of Lough Conn near the Nephin Beg Mountains, and 3 DEDs at the foot of the Ox Mountains east of Ballina. Animals with radiocaesium activities above 600 Bq, kg were measured on 10 farms in the DEDs of Srahmore, Ballycasile, Deny, Knocknalower, Seskin, Kilgarvan, Attymass East and Sallymotint. Only in the DED of Altymass East were activities above 1000 Bq kg recorded, although in the neighbouring DED of Sallymount, 8 of the 20 animals monitored on one farm were above 600 Bq'kg. The highest individual measurement was 1140 Bq kg. GALWAY/CLARE A total of 8 DEDs in Galway and 6 in Clare were visited. From a total of 888 animals monitored in Co. Gahvay, 11 (1.6%) were above 600 Bq kg. In Co. Clare, only 1 animal from a total of 619 monitored exceeded 600 Bq kg. The highest individual reading was 867 Bq kg from a ewe in the DED of Cloonusker in the Slievc Anghty Mountains, in Co. Clare. KERRY One of the most extensive county monitoring programmes undertaken was is Kerry, where 329 farms divided between 59 DEDs were visited. The area monitored included the Dingle Peninsula, the Caha Mountains in the Bear Peninsula and the Macgiihu uddy Reeks. A total number of 7649 animals were monitored, and the only significant activity delected was in the Dingle Peninsula. This area hail been subjected to significant rainfall in May 1986 during the passage over Ireland of the Chernobyl cloud, and 2 neighbouring farms in the DED of Brandon showed radiocaesium activities consistently between 600 and 1000 Bq kg. The pattern of sheep breeding and flock management in Kerry in such that, on many of the farms visited as part of this survey, animals spend much of the summer months on lower pastures, returning to mountain grazing during the winter. 10 The measurements recorded in this report, llu*rx*f<»iv, inny no! represent the maximuni radioraesium concentration in the animals, but iluvy will ho indicative of (he activity present in sheep from Co. Kerry going lor slaughter. Some limited additional monitoring on selected farms during die vviitier months would, however, lie desirable CORK A total of 117 farms in 21 DEDs in that part of Co. Cork west of a line between Skihbereen and Bandy were visited, and 2,393 animals monitored. None of the animals showed radiocaesium activities in excess of 600 Bq/kg. WATERFORD The highest individual activities recorded in 1987 were in Co. Waterford. As part of the 1988 programme, a total of 92 farms in 17 DEDs were visited, and 1402 animals were monitored. All of these grazed in the Knockmealdown and Comeragh Mountain ranges. In all, 450 (32%) animals showed measured radiocaesium activities above 600 Bq/kg, with 201 (14%) of these above 1000 Bq/kg. The highest readings were in the DED of Ballyin in the Knockmealdown Mountains. From the 125 animals monitored, 99 were above 600 Bq/kg, of which 88 were over 1000 Bq/kg. A total of 8 ewes and 3 lambs showed radiocaesium activities above 2000 Bq/kg, with a maximum reading of 2996 Bq/kg. Activities above 2000 Bq/kg were also recorded in the neighbouring DED of Ballysaggart and in the area locally referred to as "The Nire" just south of Clonmel. In the DED of Ballyin several farms, where the sheep were on lowland grazing, was monitored. Where animals had no access to heather all measured activities were less than 100 Bq/kg, while on all of the other farms in the same DED animals with radiocaesium activities above 1000 Bq/kg were identified. This is a clear example of the benefits of lowland grazing, where the low transfer of radiocaesium from mineral soils into herbage results in insignificant activity levels in sheep. TIPPERARY A total of 33 farms in 8 DEDs were monitored. The DEDs of Newcastle and Clogheen are located in the Knockmealdown Mountains, with the remaining 6 DEDs forming the Galtee Mountains. Animals with radiocaesium activities above 1000 Bq/kg were identified in both mountain ranges. A total of 725 animals were monitored, with 159 (22%) being above 600 Bq/kg, of which 32 (4% of total) were above 1000 Bq/kg. The highest individual reading was 1700 Bq/kg in the DED of Clogheen. CARLOW/WEXFORD A total of 38 farms in the Blackstairs Mountains were visited, and 724 animals were monitored. Only 1 animal exceeded 600 Bq/kg, and this was a ewe from the DED of Kiltealy in Co. Wexford, with a measured activity of 616 Bq/kg. LAOIS/OFFALY Work in these two counties involved measurements both on the lowland peats and in the Slieve Bloom Mountains. An enhanced transfer of caesium from all peaty soils has previously been demonstrated, and, even in the absence of heather, it was felt that the monitoring of a number of lowland farms where animals would graze all year round, albeit on grass, would be worthwhile. 11 Quito a number of OKDs had less than f> (aims within their boundaries, and, so, ilic number of slurp moniloied on each farm was increased to JJ^!%•«.•. where possible, a loial of KM) measurements IJt t DKD. In addition, many of the DF.Ds in Co, l.aois ate amalgamated lot Department of Agri A total of liSM animals divided between (>8 farms in 21 Dr-'.Ds were monitored. Only one animal, ill the OKI) of Clonmacnoise in Co. Olfaly, exceed (500 Bq kg. This OKI) consists predominantly of lowland blanket peats where (he animals have liillo or no access to heather. Al the end of the survey this farm was revisited and similar results were again obtained. LOUTH Five OEDS in (he Oooley Mountains north ol Curlinglord were visiicd and u total of 181 animals Oil 2-J lat'tllS W't'tV numiloicd. In a\\ Vive V>¥/Os i\vilm\s with vadiexwsium wcviviues above- 600 Be;/ kg were measured, and in the DKDs of Carlingiord, Diumullagh and Ravensdale animals above 1000 Bq kg were ideniified. A total of 91 (20%) animals exceeded 600 Bq/kg, while 25 (.r)%) of these wen- above 1000 Bq kg. The highest individual reading" was 1500 Bq/kg in flic DED of Cailingford. It should be noted that the highest deposition of caesium-!.') 1 measured immediately following Chernobyl was on a pasture outside Dundalk. The figure quoted is 14,200 Bq/nv-, compared with a weighted mean for the whole country of 3,200 Bq/nv- (1). Given the abundance of heather on the Cooley Mountains the results obtained are not surprising. 2.6 Variation in Activity between Lambs and Ewes During the four months duration of the survey, no consistent difference was noted between the activity in ewes and that in lambs. On a number of farms visited the lambs were grazing on lower pastures than many of the ewes monitored, and in these circumstances consistently lower activities were recorded in the lambs. In cases where both ewes and lambs had access to the same grazing area again no consistent pattern emerged. Of the 19 animals ideniified with radiocaesium activities above 2,000 Bq/ kg, 9 were ewes and 10 were lambs. Eight of the ewes, however, came from the same farm, while the lambs were divided between 7 farms in 4 counties. During the course of the survey, lambs of many different ages were monitored, and in the absence of a controlled experiment no scientific statement can be made on the difference in activity between lambs and ewes. As a general observation, however, in situations where both lambs and ewes have access to the same grazing area and have been grazing there for a similar length of lime, the activity in lambs would appear to be towards the upper end of the range of activities measured in the ewes. 2.7 Comparison With Results From 1987 A number of farms which had been visited as part of the 1987 monitoring programme were revisited in 1988. When the results of both sets of measurements are compared, about 30% show similar levels. The remaining 70% are almost equally divided between those which show a statistically significant increase and those which show a statistically significant decrease. A direct comparison of this nature is not particularly valid. Both studies were conducted at different limes of the year, so that the plant species contributing to the sheep's diet may be very different. In addition, there is no guarantee that animals were grazing the same upland pasture during both monitoring programmes, and on a number of farms visited this was clearly the case. It has previously been mentioned thai the radiocaesium activity in sheep will peak '•> weeks after animals commence consumption of contaminated pasture, after which it will be reduced to (i8"o of its peak concentration (()). This implies that flocks monitored timing the months of June and July are likely to be dose to their peak activities, while for (hose visited later in the year the activities will be somewhat reduced from their maximum. Comparison of results from both monitoring programmes may therefore be misleading. 12 3. STATISTICAL EVALUATION OF UPLAND FARM RESULTS .'J. I Introduction The aim of iliis siatislical analysis is to draw some conclusions about the levels of radiocaesiiim throughout a flock ;>r throughout a DEI) based on the results of measurements made on a random selection of animals within thai flock or DED Animals which are exported abroad and which are slaughtered for home consumption musi meet a criterion of 600 becquerels per kilogram (Bq. kg). In addition, the Nuclear Energy Board has set an "action level" of 1000 Bq kg. What this action level means is thai if there is evidence that sheep in mountain areas may have activities in excess of 1000 Bq kg, then there is a need to examine the situation to see what restrictive or preventive measures, if any, may be necessary. The form that any such measures might take would obviously depend on the extent and degree of contamination identified. The value, erefore, of performing statistical analysis is that it allows the identification of areas in which, even though none of the measured animals exceeded an upper threshold (i.e. 600 Bq/kg or 1000 Bq'kg), there is an unacceptably high probability that other non-measured animals might exceed this value. This may, then, indicate the need for further investigation in these areas, a programme of advice to farmers on stock management so as to reduce the levels of activity prior to slaughter, or, in extreme cases, restrictions on the movement and slaughter of sheep within these areas. 3.2 Statistical Testing The statistical test undertaken (9) as part of the in vivo sheep monitoring programme is based on the ratio K = U-X S where U = upper threshold of activity X = sample mean S = sample standard deviation The sample mean, X, is the average value of all the measurements, while the sample standard deviation, S, reflects the variation in measured activities throughout the sample. The upper threshold of activity, V, will be either 600 Bq/kg or 1000 Bq/kg, although the equation can equally well be applied to any activity threshold. The calculated value of K can then be used in conjunction wilh statistical tables to determine the percentage of sheep likely to exceed the pre-defined upper threshold. It should be noted that this calculation also lakes into account the size of sample. Clearly, measurements on 100 sheep will constitute a much firmer basis on which to draw conclusions about the remaining animals in a flock or DED than measurements on only 10 or 20 sheep. A similar statistical analysis was performed on the results of 1987 programme with a view to identifying areas in need of additional monitoring. Such areas were deemed to be "reserved", while all remaining areas were "cleared". The same terminology will be retained for this repori. The interpretation of the term "reserved", however, is different. The additional monitoring indicated by the 1987 results as being necessary has now been undertaken, and so in any areas deemed "reserved" there is a need (o consider restrictive or preventive measures. Obviously if any animal in a flock or DED has been measured as having a level of radioactivity in excess of the upper threshold, then iliai flock or DED would automatically be "reserved". Equally, if all animals monitored show non-measurable levels of ra-'iocaesium, lhat flock or DED should'be "cleared". The statistical testing, therefore, applies only lo flocks or DEDs which do not obviously 13 TABLE 2 Percentage Chance of Clearing a Flock with a Specified Proportion of Sheep above a Pre-defined Upper Threshold for a Sample Size of 20 per Flock True percentage of carcasses above the Cut off Value K threshold 2 3 4 5 6 7 8 9 10 1 in 100 000 (0.001"..) 100.00 99.09 65.02 19.11 1.12 0.91 0.23 0.07 0.02 1 in 10.000 (0.01",,) 100.00 91.03 SI 11 6.39 1.12 0.23 O.Oli 0.02 0.01 1 in 5,000 (0.02%) 100.00 81.31 25.11 -1.11 0.69 0.1 1 0.01 0.01 0.00 1 in 1,000 (0.1%) 99.72 56.69 9.25 1.16 0.18 0.01 0.01 0.00 0.00 TABLE 3 Percentage Chance of Clearing a Flock with a Specified Proportion of Sheep above a Pre-defined Upper Threshold for a Sample Size of 100 per Flock True percentage of Cut off Value K carcasses above the threshold 2 2.2 2.4 2.6 2.8 3 3.2 3.4 3.6 3.8 I in 100.000 (0.001%) 100.00 100.00 100.00 100.00 100.00 100. CO 100.00 99.95 99 23 91.18 1 in 10.000 (0.01%) 100.00 100.00 100.00 100.00 100.00 99.89 98.17 88.88 66.76 38.93 1 in 5,000 (0.02%) 100.00 100.00 100.00 100.00 99.96 98.91 91.15 70.39 •11.37 18.34 1 in 1,000 (0.1%) 100.00 100.00 99.98 99.02 90.38 (it.92 32.93 11.81 3.17 0.69 fall into the "reserved" or "< leared" category and is a way in which out" can quickly identify additional areas which should be "reserved". On the basis of sampling it is impossible to be completely sure (bat a flock or DKD has no animals in excess of any threshold value, and so die usual statistical procedure is to accept a flock or DKD as "cleared" if it is likely lo contain only a very small proportion of sheep with an activity level above the threshold. In tliis analysis (he criterion used for "clearing" a particular flock was that any flock wild more than 1 animal per thousand above the upper limit of radioactivity should have a less than 5% chance of being "cleared". This is related both to the1 calculated value of K and to the sample si/.e, and can be summarised as lollows:- For a sample v/c of u = 100. if K is less than 3.6, there is an unacceptably high probability of animals within the flock exceeding l'".1 upper threshold. For a sample' si/c ol n = 20. if K is less lhan 5.0, there is an unacccptabK high probability ol animals within the Hoc k exceeding the upper dirt sholtl. 14 Iloiks 01 DI\I)s in which these k-vjlues an- rxi ceded (.in he "cleared". In other cases, where llie < alt u latcil -v-\ a I ue is below I hose spec 11 red above, appri >pi ia!e additional ineasnu- • should be c onsidcicd. The lelcvani suilislic al lal)Ies loi sample si/cs of n = 20 and n = KM) appeal in Tables 2 and .'i. .'i.'i Results The value of K has heen calculated for cadi flock on which measurements were made. Caleiilations have heen made for upper thresholds of 1000 Bq kg and (>()() Bq kg; ihese have been called K.-I000 and K-f)()() respectively, and are quoted in the final columns of Appendix 1 al the end of this report. One of ihe essential aspects of the statistical lest previously described is the issumpiion that the results follow a normal distribution. This is the case for each set of measurements from the individual flocks. However, when the data for all farms in the same DED are combined, it is found that the results do not follow a normal distribution, primarily because of the large variation in activity levels between flocks within the same DED. For this reason K-1000 and K-600 values have not been calculated for the DED results listed in Appendix II. Instead, it is necessary to declare DEDs either "reserved" or "cleared" on the basis of the results from individual farms. For an upper threshold of 1000 Bq/kg, a total of 74 DEDs are automatically "reserved" because of at least one measured animal having an activity level in excess of 1000 Bq/kg. A further 140 DEDs tan be automatically "cleared" because each of the flocks within their respective boundaries has a K-value greater than 5.0. This leaves a further 45 DEDs in which ro measured animal has exceeded 1000 Bq/kg, but in which at least one flock has a K-value less than 5.0, which indicates that it should be "reserved". Because we have shown that it is not valid to combine all of the results on a DED basis, these additional 45 DEDs must also be declared "reserved". A similar calculation can be undertaken for an upper threshold of 600 Bq/kg. This results in 174 of the 259 DEDs being "reserved", with the remaining 85 being "cleared". 4. SLAUGHTERHOUSE MONITORING PROGRAMME 4.1 Description Of The Programme Following completion of the on-farm in vivo sheep monitoring programme in 1987, monitoring was extended to include sheep being received al slaughterhouses and destined for both the domestic and export markets. This programme commenced on Monday 1 Hh January 1988, at which lime portable survey instruments were made available to veterinary inspectors at the main slaughterhouses dealing with the export sheep market (viz Kepak Ltd., Athleague; Halal Meal Packers, Ballyhaunis; Anglo Irish Beef Packers Ltd., Ballymun; Slaney Meats, Bunclody; United Meat Packers, Camolin; Goodhurst Ltd., Dublin; and Kepak Ltd., Hackestown). A further monitor was located at Doherty Meats. Carrigans, Co. Donegal in August 1988, following the commissioning there of a new sheep line. Initially up lo 20% of all sheep passing through each plant were monitored. When the programme was reviewed in March 1988, the results which had so far been obtained and the decrease in the number of mountain sheep which would subsequently be slaughtered, justified a reduced sampling rate. The percentage of sheep being monitored was, therefore, successively reduced in subsequent months to a minimum of 2% from June onwards, with particular emphasis being placed on the monitoring of sheep of upland origin. Besides those slaughterhouses dealing primarily with the export market, sheep going for slaughter at selected outlets serving the home market were also examined nationwide. In addition, a study was 15 uiuli'i taken in (In. Coik dining the months <>( l-fbt nai \ and Mai< li by Vcteiinai\ Inspcclois ol ( !OI k County Coutu il. m\oi\ ing if x1 measurement .2 Results The results ol the programme an1 summarised in Table 1, and are represented graphically in Figure 2. from a toial number <>' 16,001 animals monitored. 44,693 (97°o) showed activities below 100 Bq kg. More than 99.5% ol the animals monitored showed activities below 200 Bq kg. A total ol 4 animals exceeded 600 Bq kg; these were withdrawn from slaughter and were returned to ihe farmer for lowland finishing. The highest activity animals were from counties Donegal. Galway, Mayo. Roscommon and Offaly. In some other cases, because the sheep had been purchased through a dealer rather than directly from (he farmer, their exact origin could not be determined. TABLE 4 Results of Slaughterhouse Monitoring January - December 1988 Number of Animals for each range of activities (Bq/kg) Slaughterhouse <100 100-200 200-300 300-400 400-500 500-600 >600 Athleague 5416 362 65 20 7 Ballyhaunis 2654 108 9 4 3 1 2 Ballymun 3496 50 5 1 Bunclody 8742 155 3 Camolin 8786 120 2 Goodhurst 4527 62 2 Hacketslown 3667 99 2 3 Carrigans 255 56 5 2 Domestic Outlets 7150 152 11 TOTAL (46004) 44693 1161 102 28 12 1 1 16 FIGURE 2 Distribution of Radiocaesium Activities in Sheep being received at Slaughterhouses. 0 — 100 Bq/k3 100 — 200 Bq/kg > 200 Bq/kg 5. LABORATORY ANALYSIS OF SHEEPMEAT FROM BUTCHER'S SHOPS During the months of April/May and October/November 1988 samples of sheepmeat purchased from butchers' shops nationwide were submitted to the Board by the eight Health Boards, by Dublin Corporation and by Dublin County Council. The samples were analysed in the Board's laboratory by high resolution gamma spectrometry, and the results of these analyses are summarised in Table 5. AH but 9 of the 223 samples analysed had measured total radiocaesium (combined caesium -137 and caesium-134) activity less than 20 Bq/kg. The highest individual measurements were 83 Bq/kg from a ewe which had previously grazed on heather in the Cooley Mountains, and 124 Bq/kg and 298 Bq/kg respectively from 2 animals which had been on upland grazing in (lie Renvyle area of Co. Galway immediately prior to slaughter. TABLE 5 Radiocaesium in Lamb Samples January — December 1988 Origin No. Of Samples Mean Range Bq/kg Bq/kg North-Eastern Health Board If) 12.3 4 — 93 Eastern Health Board 29 7.1 4 — 16 Souih-Eastern Health Board 27 6.8 •1 — 14 Southern Health Board 37 8.1 2— 36 Mid-Western Health Board 23 7.5 4 — 15 Western Health Board 28 27.6 5 — 298 Nonh-Wester.i Health Board 10 8.2 1 — 20 Midland Health Board 11 7.9 3— 26 Dublin Co. Council 5 6.2 6— 7 Dublin Corporation 8 6.0 :-)- 7 17 6. RADIATION DOSES TO CONSUMERS A toial <>l 800.000 sheep is slaughtered lor home consumption every year. Of these, 96,000 are mountain sheep from (he areas which have been .subject to monitoring. While the majority of mountain sheep destined for the home market would undergo normal finishing on lowland prior to slaughter, one must recognise that in the absence of restrictions on the movement and slaughter ol sheep and in spite of monitoring at slaughterhouses a certain number of animals may pass directly into the loodehain. In some cases this may be as a result of butchers purchasing directly trom hill tanners, with the meat subsequently being sold to a number of customers across the counter. In oilier instances, in entire carcass may be stored in a deep freezer for consumption ai regular intervals during the following months. The group of people likely to be exposed to the highest radiation dose (called the "critical group") are (hose hill fanners and their families who kill and subsequently freeze their own sheep for regular consumption throughout the year. On a total of .SI of the farms visited, the mean activity measured in the flock was in excess of 1,000 Bq kg, with a maximum of 1,800 Bq/'kg- If this peak value is combined with an assumed critical group annual consumption rate of 30 kgs, the tola] ingested activity per individual of 5 1,000 Bq, with a resultant annual effective dose equivalent of 0.76 millisievert (mSvj. For the average consume], the results ol the analysis of samples of sheepmeat from butchers' shops indicate a mean annual effective dose equivalent of .0009 mSv (0.9 mioosieverls). This figure is based on an annual consumption rate of fi.8 kgs (10) and uses the population weighted mean activity in sheepmeat of 9.5 Bq kg, calculated from the data in Table 5. A preliminary estimate of .00057 tnSv had been made on the basis of 63 samples analysed during the first six months of 1988 (5). The slightly higher figure of .0009 mSv now quoted is a result of the analysis of sheepmeat of known upland origin submitted during October/November 1988, the results from which have now been incorporated in the calculations. The principal dose limit for members of the public recommended by the International Commission on Radiological Protection (ICRP) is 1 mSv per year over and above natural background. The Commission feels that a subsidiary dose limit of 5 mSv per year can be applied in certain emergency situations, provided that the practice giving rise to the exposure is of short-term significance. It is, therefore, considered prudent that the annual effective dose equivalent arising from the consumption of sheepmeat should not exceed I m.Sv. In the case of those hill farmers deemed to constitute the critical group, their annual effective dose equivalent would be 76% of the ICRP recommended dose limit, while the dose which would be received by the average consumer would be less than 0.1% of this limit. It is therefore concluded that the regular consumption of sheepmeat does not represent a significant radiological health hazard. For comparison purposes, it is worth noting that the average annual effective dose equivalent to members of the Irish population from natural background radiation is 2.6 mSv. In cases where individuals live in areas of high natural radioactivity this annual dose may be up to 30 times higher (II). TABLE 6 Radiation Doses to Members of the Public Exposure Pathway Effective Dose Equivalent (mSv) Average Consumer 1. Consumption of 6.8 kg of lamb 0.0009 with a mean activity of 9.5 Bq kg Critical Group 2. Consumption of 30 kgs of lamb 0.76 with a mean activity of 1,800 Bq kg Natural Background Radiation 3. Mean annual effective dose 2.6 equivalent in Ireland 18 7. CONCLUSIONS AND RECOMMENDATIONS I I he on-lann moniloiing programme has identified 1.021 animals uilh i.idioc aesiinn a< ii\ ilies above 1000 I5() kg on 158 larms in 75 of ihe 259 DFDs visited. This represents .'}.8"« ol the loial niimhci ol animals monitored. Considerable variation within Hocks and between dilfeteni Hoiks in the same DF.I) was recorded. 2 The normal finishing process. In which moiiniain slurp spend up to 12 weeks on lowland gra/ing prior to slaughter, is an effective method of reducing the radiocacsium levels in the animals. Over 99.5% ol animals monitored at slaughterhouses showed activity levels below 200 Bcj kg, and only 1 Irom a total oi 16,001 monitored animals exceeded 600 Bq kg. In addilion, laboratory analysis ol sheepmeat sold over butchers' counters showed a mean activity level of 9.5 Bcj kg lor 223 samples analysed during the month of May 1988. 3 Less (Man 2O°o of sheep produced annually lor home consumption are of upland origin, and the majority of these would undergo normal lowland finishing prior to slaughter. In the extreme case, where hill farmers in the worst affected areas kill directly from the mountain and subsequently consume sheepmeat in large quantities throughout the year, (he annual dose limit of 1 millisievert as recommended by the International Commission on Radiological Protection (ICRP) would no! be exceeded. The doses which would be received by the average consumer would be less than 0.1% of this ICRP limit. Consequently il is concluded that the regular consumption of sheepmeal does no! represent a .significant radiological health ha/aid. 1 For certain specific- export markets some animals may come directly from upland grazing to the slaughterhouse without undergoing the normal finishing process. As many of these animals are produced in areas identified as having elevated activity levels, continued vigilance will be necessary to ensure thai exports comply with the 600 r>q/kg limit laid down by the EEC. 5 It is considered that a heightened awareness among the farming community of the benefits ol lowland finishing as an effective means of reducing the activity in mountain sheep would be desirable. Considerable data are now available on radioactivity levels in all upland areas; the farmers in each affected DED should be contacted and advice should be available through the Department of Agriculture and Food as to how Hockowners can ensure that all sheep being presented for slaughter are within the prescribed limits. 6 The monitoring programme presently being undertaken at slaughterhouses will need to continue for the forseeable future. Those responsible for monitoring should concentrate on mountain sheep coming from those areas known to be affected. It is proposed that 2% of all sheep passing through slaughterhouses be monitored, with this figure being increased to 10% for groups of animals of known upland origin. 7 The implementation of restrictions on the movement of sheep is considered to be neither necessary nor desirable. The highest levels recorded in Ireland are considerably less than the peak activities reported for parts of the United Kingdom, and the normal finishing process ensures that these levels are even further reduced prior to slaughter. With regard to the small number of animals found to have unacc eplably high radioactivity concentrations, in vivo monitoring at slaughter points has allowed these to be returned to the individual farmer. 8 With regards to on-farm monitoring in future years, there is little repeating the extensive programme of work undertaken in 1987 and 1988. It is proposed that a small number of farms deemed to be representative of each upland area be selected for detailed investigation. This would include not only monitoring of the activity in the sheep, but also measurements on soil, heather and other upland plants consumed with a view to establishing the mechanisms of uptake and transfer of radioactivity. These farms would continue to be monitored in successive years so that temporal variations in activity could be determined 19 8. ACKNOWLEDGEMENTS I lie aulliois would like lo (lunik oliicials ol ihc D<'|>ailiiuuts ol Agric iilluic ami Food and of Health lor then co-operation in completing the programme ol work outlined in this icpon. Main ol then olficers provided assistance well in excess ol what one might icasoiiahly expect, and their haul work and professionalism brought considerable credit to both Dcpar.menis. In addition, (he excellent co- operation received from the fanning community and. in particular, horn the llockowneis \isited as part ol the monitoring programme is gratefully ac knowledged. Many ol the stall of the Nuclear Energy Board were directly involved in the programme. Special thanks are due lo Barry Dunne, who was responsible lor muc h of (he compuier programming, and lo John O'Crady and I .onaine din ivan, who assisted with the training ol field staff. J he radiocaestum analysis ol sheepmeat samples was undertaken at the Board's environmental laboratory under the direction ol (.cialdinc Me Neill and Mairin O'Colniain. The manuscript was typed by Catherine Dunning, whose patience and understanding is much appreciated. We also thank the Board's Environmental Radiation Advisory Committee, as well as scientists working in other institutions both at home arrd abroad for their valuable ad-ice aitd direction. 20 9. REFERENCES 1. M( ALLAY. J.R. and MOR.W. I).. 1989. K:nli<>( ;icsiuiii hilloul in Inland liom the Cheniobvl \i( idem. J. Rmliol. I'),,I. Vol. !)( 1 ) '1\)-:V1. 2. MITCH1 I.I . P.I.: SWCIIl/CABi /A. J.A.; RYAN. IP.: M< CARRY. A. I and VIDA1 .-(.MADRAS. A.. 1988. Piiliminai> l-.slinialcs ol CaimnLili\i- Caesium and I'lnionnitri Deposiiio» ID il;i- liish Teitestiial F.iiviionmeut (In |»css). S. MacNF.ILL. (..: DIIIV, J.; (Oil TI'R. B.: DIAMOND. S.: M.ATI.AY I.R. ami Cl "N\I\{;HAM. J.D.. IfWH. R 1. COIXiAN. I'. A.. IWH. A Kcpon on llic Levels ol Radioi aesinni Aclivilv in Mountain Sheep: Oclober- Deoinhei h)87. N'iuieai KneigA Board. Dublin. j COI.GAN. P.A. and SCl'I.I.Y. B.J. l<)88. Sheep Moniioiin.u Pio.^aimrie lamiaiv — Scpicnihi-i MISK. Nuclear l"'.ncrj>y Board. Dublin. (). WAI.TKRS, B.. 1988. Chernobyl Derived Adivily in Slieep: Yanalion within a Single Flcnk and with Time. J. Emnroii. Radioa 7. MKRKDITII, R.C.; MONDON. K.J. and SlIKRl.OCK. J.C.. 1988. A Rapid Melhod for ihe in nvo Monitoring of Radiocaesiuin A< livily in She;]). J. Environ. Radioactivity, Vol. 7. 209-21-1. 8. SIIKRI.OCK J; ANDRFAVS. D.; Dl'NDKRDALK. J.: I .ALLY, A. and SHAW. P.. 19«8. The in vivo Measurement of Radiocaesium Activity in Lambs. /. Environ. Radioactix'ity, Vol. 7. 215-220. 9 Dt'NCAN. A.J. I9f)5. Quality Control and Industrial Statistics (R.D. Invin. Illinois). 10. CKNTRAL STATISTICS OFFICH, 1987. Supply and I'lilisation Balance sheets. 11. MrLAUGHLIN, J.P. and W'ASIOLF.K. P., 1987. Radon Levels in Irish dwellinss. Pain-r presented at the 111) International Symposium on the Natural Radiation Knvhonment. Lisbon, Portugal. 7- 11 Dei ember 1987. 21 Glossary of Terms 1 . K. 1111 o. 11 11 \ 11 \ 1 In pi i >pci l\ i it i. id ion I ii hdcs ol spot il.ii icon si \ ruin 11 IIL; loijjzing l.uli.ilu HI 2. Ionizing K.uli.iiion Radiation u hie h I ha ngcs the pi I\ SIC a 1 stale ol atoms u hie II II sin kcs. c a using 11 Kin lo he (!(•( II ic all\ (hatred. Is < ailed ionizing jadiaI ion. I he piescnccof c hatged atoms in li\ ing lissiic-s c an disiupf uonnai biological pi oe esses. |ns( as cxposuie lo olhet loiins ol ladialion I i.e. sunlight, in it IO waves. ulna\ iolei light) c an do haim. ionizing ladiaiion max lepsesetii a lie.dlh lia/aid lo man. A«li\it\ I'lie lenn ",Kli\il\" is ihe quantilv ol a ladiomic lieic. It defines (lie tale a I u Ini h spoil l.ineoi is em issii >n o( ( ins. and is ineasined in lice <) net els. 1. Radioniu liele- An unstable alom. with specific unclcai e haiae iciistie s. dial emits ionizing ladiaiion. 5. llall-lili Ilie lime taken lo| die .n 11 \ 11 \ < >1 a pailuulai ladloitiit tide lo he hahed. I lie pioiess UIIKII leads lo a ledutlloli in aili\il\ with lime is called tadioaclivc de( a\. Diflctcnl tadioiiue li 6. Biological When radioniu lides are present in a hiolo^ual SASU'IH. ihey ran be Uall-iife eliminaled from dial sysit-n \»\ melal)oli< plot esses, as wel! as J>y tadioa< li\e de 7. Isolope Dilicrcnl atomic lorms of the same element arc- called isoiopes e.s;. caesium— I.S7 .md < aesium-I.S I: lead-21 I and lead-210. Some isoiopes ale stable while olheis aie ladioac live. 8. Caesiuin-1'57 An isotope ol caesium with a hall-life ol approximately .SO years. 9. Caesium-1.S 1 An isotope ol caesium with a hall-life ol approximately 2.1 years. 10. Dose At;eneiai lent! denoting a c|(ian(ii\ of energy imparled l>\ ioni/ing ladiaiion. It is usually qualilicd as absorbed dose, dose equivalent or effective- dose- ec]iii\alelil. 11. H.ffec live De.se The cjiianlification ol dose which lakes ace ouni of (he effectiveness of vat ions Ivpes of ionizing radiation in causing harm arid allov.s for the dilleling sensilix iiies ol dilfeie-nt otgans and tissues to ionizing ladiaiion. r.lfec live dose equivalent is measured in Sieveri. 12. Bc-cc|uerel (Hep The unil in wliii Ii activity is measuieel. Ii lepiesents 1 disintegralioii per se( ond. 13. Sieveri (Sv) I'lie unit in wliie h e-ffec ti\c- close ec|iii\alent is measured. 14. tnilliSieveitdtiSvi One thousandth ol a Sievcrl. 15. mil ioSie\eti ( JJ.S\ ) One milliouih ol a Sicvcil. 22 APPENDIX 1 RESULTS OF ON-FARM MEASUREMENTS 23 Key to farm "flags" * Animals have minimal access to heather •• Animals on lowland grazing *** Mixed grazing-rough grass and heather **** Animals measured divided between t'piand and lowland grazing + Animals divided between two different hills + + Animals on lowland grazing (or up to one week prior to measurement ERR K-value not defined ^ r i,_ o T c f- c t" i-j c> w C- v E> t- rj «-. G3 ! i". PJ v rM ^ c t«j »i rj r. : .fi«-*-*f[©0 00©00'f'*tfs*—•O000000--"r'iirj— O © O O rj *- i o o O ffl *™ *-• •TJ «-* •-* *— f J — r» o •C1 c- o rs r* r» ^ n o f) o r n-* f« r s ^? o o o a rs o * o * — ra in — 9^* T ffl£ • fi -- — — t,t o o fa — — —• n o «•». c* « ru o uuuuu xxxxxxx->->->- XXXXX XSZ ; ui uitn in ececcuuuuuuuu _ « < OOO x x x cc a »c c c c ^ UOOUCJO-I-l-J-l^ ZZZ2ZZ-1-J-1.J E S 5C »: >C C U O OOOOO O O O •-• r* r* r+ r+ ** f OOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOOO r i « i i I I i I j I i I ii I I 1 I i i i * I s 1 « < » I i * « ( * i a n j ^ j ,t t ) I ) j w c> w c> c* c* c* uGuMMMca O C C CC C (- U U U I 2Z23:2222222ZZZ2222222Z z z z :• OOOODOOOCJOCM QOOOOO OOC0COO0O0COOOOO 25 Kit'"it. nil jr./.i OV1!< COUNTY FLAG FAfcrt NO.'S D . E . P . HO. or SHEKP n IN f.t.X 1,00 i-q.'C'j 1000 !•()/! •-j 1 ICC!' DONEGAL PL-047 GLENLEHEEN 25 700 1357 2T- 1 1 0. 1 DONEGAL PL-04. FINTOUN 24 164 •;t7 G 0 DONEGAL AAA PL-O49 FINTOUN 21 0 ')24 n 0 DONEGAL PL-050 FINTOUN 25 355 O'.'l 12 0 DONEGAL AAA PL-051 ALTNAPASTE 19 722 s v/? 10 1 .! . ", ' •; DONEGAL PL-052 ALTNAF'ASTE 25 376 14 14 23 7 0 . .'. \ ' . DONEGAL PL-053 ALTNAPASTE 25 423 1449 la (, 0 . 7 DONEGAL PL-054 ALTNAPASTE 25 702 1775 2t. 16 -0.4 , DONEGAL PL-055 ALTNAPASTE 25 0 973 13 0 1 .'? ; . c DONEGAL PL-056 ALTNAPASTE 25 359 1018 ;i 1 1 .4 1 . c DONEGAL AAA PL-057 CLOGHAN 15 0 538 0 0 4 . 7 c DONEGAL PL-058 CLOGHAN «o 983 2053 25 24 - 3 .'? ; _ { LlONEGAL PL-059 CLOGHAN 25 624 1043 j '.' DONEGAL A PL-Gi' CLOGHAN 25 242 548 n 0 e. •« DONEGAL DL-061 CLOGHAN 25 608 2077 25 -o.i- J , ' DONEGAL DL-062 GLENTOGHER 25 0 675 4 0 1 . C DONEGAL PL-063 GLENTOGHER 25 0 362 0 0 U'.fc (-.. •' DONEGAL AAA PL-064 GLENTOGHER 25 0 363 0 0 \>. 7 DONEGAL PL-065 GLENTOGHER 25 105 6>?4 6 0 3 . 7 r t !• DONEGAL AAA PL-066 GLENTOGHER 25 211 69S 3 0 4 . 2 , ' , DONEGAL A PL-067 GLENTOGHER 25 0 174 0 0 It .G DONEGAL PL-0C8 GRAFFY 25 447 1552 20 15 -0.1 • 1 . '"• DONEGAL PL-069 GRAFFY 25 603 1314 2* 13 0. 0 IS) DONEGAL PL-070 GRAFFY 25 796 1537 2t IB -O.fc 0> DONEGAL PL-071 GRAFFY 25 333 922 19 0 - 0. •! DuNEGAL PL-072 GRAFFY 25 328 1096 15 1 .3 -0.4 DONEGAL DL-073 TAUNAUULLY 25 320 1026 10 1 2 . 3 C . 2 DONEGAL PL-074 TAUNAUULLY 25 306 1 151 16 1 2. 1 - 0. '• DONEGAL AAA PL-075 TAUNAUULLY 25 0 636 1 0 A.2 1 . e DONEGAL + + PL-076 TAUNAUULLY 25 115 556 0 0 5.5 .": . 1 DONEGAL AAA DL-077 TAUNAUUl.LY 25 115 509 0 0 7.6 3 . " DONEGAL PL-07H LOUGH ESK;1 25 170 499 0 0 a.o 1 _ g DONEGAL PL-079 LOUGH ESKE 7 267 515 0 0 7.0 3 . 0 DONEGAL DL-080 LOUGH ESKE 25 103 735 1 0 4.7 1 ."3 DONEGAL PL-081 LOUGH ESKE 25 234 566 0 0 :. o DONEGAL PL-082 LOUGH ESKE 25 218 6B2 9 0 3.8 o. - DONEGAL AAA DL-083 TEHPLECARN 25 171 632 1 0 S. 1 1 . « DONEGAL HL-0B4 TEHPLECARN 25 214 1463 16 3 1 .0 -0.3 DONEGAL AAA PL-085 TEHPLECARN 25 0 484 0 0 5.5 DONEGAL PL-086 GR0U3EHALL 25 349 927 14 0 -o.: DONEGAL PL-087 GROUSEHALL 25 360 961 19 0 2.9 -0. A DONEGAL AAA DL-088 GR0U5EHALL 25 0 403 0 0 7.9 4. 0 MONEGAL AA tiL-089 GROUSEHALL 2S 0 •100 0 0 29.1 17.1 DONEGAL A t'L-090 GROUSEHALL 25 0 299 0 0 10.6 DONEGAL t'L-091 LETTERMORE 25 351 1519 IB 7 0.7 -0 . 7 DONEGAL PL-092 LETTERI10RE as 722 1508 25 17 -0.3 - 2 . 5 DONEGAL PL-093 l.ETTE&MORE 25 213 1166 19 3 1 .3 -0.6 RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S n. E . D . NO. OF SHEEP MIN MAX 600 Eiq/K3 1000 bq K-1000 K - 6 0 0 DONEGAL DL-094 LETTERMORE 77 4 1859 25 23 -1 .2 -2.6 DONEGAL DL-095 LETTERMORE 0 441 0 0 7.4 3.7 DONEGAL DL-096 TERMON 479 893 23 0 2.4 -1.1 DONEGAL DL-097 TERMON 293 1231 19 6 0.9 -0.7 DONEGAL DL-098 TERMON 0 713 4 0 3.4 1 . 4 DONEGAL DL-099 TERMON 241 1022 15 1 2. 1 0.0 DONEGAL Akk DL-100 GLEN 349 1271 12 3 1 .3 -0.4 DONEGAL AAk DL-101 GLEN 0 659 2 0 3.8 1 . 0 DONEGAL Akk DL-102 GLEN 223 851 1 0 4.4 1 . 4 DONEGAL DL-103 GLEN 0 2^9 0 0 9.7 5.4 DONEGAL DL-104 PETTIGO 259 1485 17 8 0.6 -0.7 DONEGAL DL-105 PETTIGO 614 1370 25 12 0.0 -1 .7 DONEGAL DL-106 PETTIGO 745 1267 25 4 0.8 -1.8 DONEGAL Akk DL-107 EANYMORE 331 1188 14 2 1.7 -0.3 DONEGAL kkk DL-108 EANYMORE 169 1015 20 1 1.9 -0.4 DONEGAL AkA DL-109 EANYMORE 491 1433 22 6 0.7 -1 . I DONEGAL kkh DL-110 EANYMORE 425 1150 20 7 0.8 -1. 1 DONEGAL Akk DL-111 EANYMORE 0 927 17 0 2.1 -0. 1 HONEGAL DL-112 LAGHY 0 261 0 0 11.4 6.0 DONEGAL DL-113 LAGHY 137 979 12 0 1.9 0. 2 DONEGAL DL-H4 LAGHY 452 1213 23 4 0.8 -1.2 DONEGAL kkk DL-115 LAGHY 536 1069 24 2 1.7 -1.5 DONEGAL k DL-116 GOLAND 0 547 0 0 6.2 2.8 DONEGAL A A A DL-117 GOLAND 167 826 11 0 2.5 0.3 DONEGAL DL-118 GOLAND 254 1145 20 3 1.1 -0.6 DONEGAL DL-119 GOLAND 203 590 0 0 5.7 2.0 DONEGAL DL-120 CREENASMEAR 722 1609 25 19 -0.7 DONEGAL DL-121 CREENASMEAR 407 1177 13 1 1.9 -0. 3 DONEGAL DL-122 CREENASMEAR 864 200i ^5 17 -0.9 -2.0 DONEGAL + + DL-123 CREENASMEAR 26G 709 *? 0 4.1 1.0 DONEGAL DL-124 CREENASMEAR 115 1044 12 1 1.5 0.2 DONEGAL DL-125 tiOOISH 1026 1854 25 25 -4 . 5 DONEGAL k DL-126 DOOISH 387 1310 18 1 .4 -0.5 DONEGAL DL-127 DOOISH 0 286 0 0 11.3 6.0 DONEGAL DL-128 DOOISH 497 1422 22 12 0.2 -1.4 DONEGAL Akk DL-129 DOOISH 133 792 8 0 2.5 0. 4 DL-130 DONEGAL DOOISH JO 216 1591 21 8 0.4 -0.8 DONEGAL kkk DL-131 CLOGHER 0 1060 8 1 1.9 0.2 DL-132 25 DONEGAL CLOGHER 25 572 1287 23 4 0.8 -1.4 DONEGAL DL-133 CLOGHER 605 1627 25 20 -0.8 -2.6 DL-134 25 DONEGAL CLOGHER 25 340 1557 22 13 0.1 -1 .2 DONEGAL kkk DL-135 CLOGHER 0 682 3 0 3.6 1.3 DL-136 25 DONEGAL TULLYNAUGHT 25 275 826 4 0 3.8 0.9 DONEGAL DL-137 TULLYNAUGHT 0 781 7 0 2.8 0.5 DL-138 25 DONEGAL kkk TULLYNAUGHT 25 378 1697 23 17 -0.3 -1.6 DONEGAL DL-139 TULLYNAUGHT *>9 218 1139 12 1 1.7 -0.2 DONEGAL AAA DL-140 TULLYNAUGHT 266 938 7 0 2.6 0.3 RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S II. E . Ii. NO. OF SHEEP M1N MAX 600 Bq/Kg 1000 Bq/Kg K-1000 K-600 DONEGAL DL-141 DOOCHARY 25 473 1069 21 1.9 -0.9 DONEGAL k DL-142 DOOCHARY 25 279 902 4 0 3.0 0.6 DONEGAL AAA DL-143 DOOCHARY 25 458 780 13 0 4.5 -0.3 DONEGAL AAA DL-144 CLOGHAN 25 734 1762 25 19 -1.0 -2.2 DONEGAL DL-145 CLOGHAN 342 1238 21 7 0.7 -1.1 DONEGAL DL-146 CLOGHAN 25 464 1554 22 17 -0.2 -1.6 DONEGAL DL-147 GRAFFY 25 459 1305 23 13 0. 1 -1 .6 SLIGO so-ooi BRANCHFIELn 20 0 133 0 0 27.3 16.2 SI. IGO SO-002 BRANCHFIELD 20 0 <100 0 0 ERR ERR SLIGO AA SO-003 BRANCHEIELD 20 0 128 0 0 29.7 17.1 SLIGO AA SO-004 BRANCHEIELD 20 0 130 0 0 28.1 16.5 SLIGO A SO-OOf. SKREEN 30 0 675 1 0 5.3 2.9 SLIGO A SO-007 SKREEN 30 0 564 0 0 4.8 2. 1 SLIGO SO-008 SKREEN 20 183 1015 3 1 2.8 o.a SLIGO SO-009 SKREEN 20 243 800 6 0 2.7 0.5 SLIGO SO-010 TEMPLEBOY STH. 20 366 824 7 0 3.3 0. 3 SLIGO + SO-011 TEMPLEI'OY STH. 20 130 1015 17 1 1 .4 -0.7 SLIGO + SO-012 TEMPLEBOY STH. 20 378 1668 18 10 0.0 -1.1 SI. IGO + SO-013 TEMPLEBOY STH. 18 342 1246 12 5 0.9 -0.7 SLIGO SO-014 TEMPLEBOY STH. 22 0 453 0 0 9.6 5.4 SLIGO AA SO-015 BUNCROUEY 20 0 <100 0 0 ERR ERR SLIGO kkk SO-016 BUNCROUEY 20 205 713 5 0 3.7 0.9 SLIGO A A SO-017 BUNCROUEY 17 0 135 0 0 25.3 14.3 SLIGO *A SO-018 BUNCROUEY 20 0 672 1 0 3.2 1 .5 SLIGO SO-019 BUNCROUEY 20 243 583 0 0 7.3 2.8 SLIGO AAA SO-020 ACLARE 19 0 624 1 0 4.2 2. 1 S1.IG0 kk SO-021 ACLARE 18 0 284 0 0 9.6 5. 1 SLIGO SO-022 KILMACTEIGE 20 0 366 0 0 7.4 3. 7 SLIGO SO-023 KILMACTEIGE 20 0 340 0 0 8.1 4.2 SLIGO k SO-024 KILMACTEIGE 19 0 306 0 0 10.2 5.5 SLIGO SO-025 KILMACTEIGE 20 294 860 4 0 3.7 0.7 SLIGO SO-026 KILMACTEIGE 20 128 366 0 0 11.2 5. 4 SLIGO A* A SO-027 BREENCORRAGH 20 296 533 0 0 8.7 3.0 SLIGO SO-028 BREENCORRAGH 20 137 670 3 0 3.6 1 . 2 SLIGO SO-029 BREENCORRAGH 20 212 578 0 0 6.9 2.9 SLIGO SO-030 BREENCORRAGH 20 424 1453 16 1.1 -0.7 SLIGO S0-03I BREENCORRAGH 20 289 646 4 0 5.1 0.8 SLIGO SO-032 GLENDARRAGH 20 786 1559 20 14 -0.5 -2.5 SLIGO kkk SO-033 GLENHARRAGH 20 308 1188 14 2 1.2 -0.6 SLIGO kkk SO-034 GLENDARRAGH 20 161 699 4 0 3.6 1.0 SLIGO SO-035 GLENDARRAGH 20 161 603 1 0 4.7 1.9 SLIGO SO-036 GLENDARRAGH 20 106 641 1 0 5.3 2.1 SLIGO SO-037 MULLAGHERUSE 20 335 764 6 0 4.0 0.4 SLIGO SO-038 MULLAGHERUSE 20 255 776 3 0 4.5 1 . 2 RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S D . E . 0 . NO. OF SHEEP MIN MAX 600 1000 K-1000 K-600 SI.IGO SO-039 MULLAGHERUSE 20 125 668 1 0 3.7 1.4 SLIGO AAA SO-040 MULLAGHERUSE 20 263 668 4 0 4.3 1 .4 SLIGO S0-04I MULLAGHERUSE 20 345 656 4 0 5.9 1 .1 SLIGO AAA SO-042 CLOONACOOL 20 0 164 0 0 18.5 10.7 SLIGO AAA SO-043 CLOONACOOL 20 0 164 0 0 19.7 11.2 SLIGO AAA SO-044 CLOONACOOL 20 0 680 1 0 4.2 SLIGO AAA SO-045 CLOONACOOL 20 0 152 0 0 23. 1 13.7 SLIGO SO-046 CLOONACOOL 20 0 176 0 0 19.1 11.0 SLIGO A SO-047 TEMPLEVANY 17 0 <100 0 0 ERR ERR SLIGO A SO-043 TEMPLEVANY 20 0 157 0 0 22.9 13. 4 SLIGO AAA SO-049 TEMPLEVANY 20 0 176 0 0 16.0 9.0 SLIGO SO-050 TEMPLEVANY 20 125 747 1 0 4.5 1 .9 SLIGO A SO-051 TEMPLEVANY 20 0 164 0 0 26.7 15.0 SLIGO AAA SO-052 LOUGHIL 20 101 304 0 0 12.5 6.1 SLIGO AAA SO-053 LOUGHIL 20 682 1275 20 10 -0.1 -2.8 SLIGO AA SO-054 LOUGHIL 20 0 <100 0 0 ERR ERR SLIGO A A SO-055 LOUGHIL 20 0 292 0 0 13.7 7.4 SLIGO A SO-056 SHANCOUGH 20 0 <100 0 0 ERR ERR SLIGO AAA SO-057 SHANCOUGH 21 108 677 1 0 4.0 1 .6 SLIGO AAA SO-058 SHANCOUGH 20 205 374 0 0 13.4 5.8 SLIGO AAA SO-059 SHANCOUGH 20 193 468 0 0 9.0 3.6 SLIGO AAA SO-060 SHANCOUGH 20 824 2229 20 19 -1.5 -2.6 SLIGO AAA SO-061 BALLINASHEE 20 328 776 7 0 3.7 0.4 SLIGO SO-062 BALLINASHEE 20 0 805 2 0 3.0 1.1 SLIGO SO-063 BALLINASHEE 20 318 930 9 0 2.4 0.0 SLIGO AAA SO-064 BALLINASHEE 20 0 •aoo 0 0 ERR ERR SLIGO A S0-0&5 BALLINASHEE 14 0 <100 0 0 ERR ERR LEITRIM AA LM-001 DRUMAHAIRE 20 0 <100 0 ERR ERR LEITRIM A LM-002 DRUMHAIRE 20 0 190 0 18.6 10.7 LEITRIM A LM-003 DRUMHAIRE 20 0 <100 0 ERR ERR LEITRIM AA LM-004 DRUMHAIRE 20 0 260 0 13.1 7.6 LEITRIM AAA LM-005 DRUMHAIRE 20 557 1521 19 0.1 -1.3 LEITRIM A LM-006 KILLANUMERY 20 0 <100 0 ERR ERR LEITRIM A LM-007 KILLANUMERY 20 0 183 0 19.0 10.5 LEITRIM AAA LM-008 ARIGNA 20 0 294 0 10.3 5.8 LEITRIM AAA LM-009 ARIGNA 20 0 157 0 19.2 11 .3 LEITRIM AAA LM-010 ARIGNA 20 0 284 0 13.9 7.5 LEITRIM AAA LM-011 ARIGNA 20 0 116 0 37.2 22. 1 LEITRIM AAA LM-012 ARIGNA 20 0 1188 8 1.4 0.2 LEITRIM A LM-013 KILLARGUE 20 0 248 0 13.3 7.4 LEITRIM A LM-014 KILLARGUE 20 0 742 1 4.4 2.3 LEITRIM A LM-015 KILLARGUE 20 0 <100 0 ERR ERR LEITRIM A LH-016 KILLARGUE 20 0 752 2.7 0.9 LEITRIM AA LM-017 KILLARGUE 20 0 224 17.7 9.9 KA N b li ANIMALS OVER CUUNTY FLAB FARM NO.'S D . E . D . NO. OF SHEEP Mill MAX 600 Bq/Kg 1000 Fq/Kg K-1000 K-600 L E 11R IM AAA LM-018 MAHANAGH 20 147 615 0 4.8 1 . 5 LEITRIM AAA LM-019 MAHANAGH 20 0 706 1 0 4.7 2 . 1 LEITRIM AA LM-020 MAHANAGH 15 0 287 0 0 9.3 5 . 1 LEITRIM AAA LM-021 MAHANAGH 20 0 740 1 0 3.8 1 . 6 LEITRIM A LM-022 MAHANAGH 20 0 289 0 0 10.5 6. 0 LEITRIM LM-O23 ST.PATRICKS 21 347 1138 11 1 1 .8 -0.2 LEITRIM LM-024 ST.PATRICKS 18 0 230 0 0 10.9 6. 2 LEITRIM A A LM-025 GLENBOY 20 0 •a oo 0 0 ERR ERR LEITRIM AA LM-026 GLENBOY 20 0 •a oo 0 0 ERR ERR LEITRIM AA LM-027 GLENBOY 20 0 123 0 0 34.8 20. 6 LEITRIM AA LM-023 GLENBOY 20 0 169 0 0 18.2 10.3 LEITRIM LM-029 GLENBOY 20 287 793 10 0 2.7 0 . 3 LEITRIM LM-030 CLOONCLARE 20 0 1075 14 1 1 .6 -0.2 LEITRIM LM-031 CLOONCLARE 20 318 1391 16 3 0.7 -0.9 I.EITRIM LM-032 CLOONCLARE 20 376 1224 16 3 0.8 -0 . 8 r* *? LEITRIM AAA LM-033 CLOONCLARE 0 2152 6 1 1 .2 0 . 3 LEITRIM AAA LM-034 CLOONCLARE 21 0 899 •> 0 3.5 1 .7 LEITRIM AAA LM-035 M'HAMILTON 20 104 1015 12 1 1.6 -0.1 LEITRIM LM-036 M'HAMILTON 20 354 1263 12 3 1 .3 -0.3 LEITRIM AAA LM-O37 M'HAMILTON 20 147 853 3 0 3.1 1 . 0 LEITRIM AAA LM-038 M'HAMILTON 20 o 603 1 0 4 .2 1 . 9 LEITRIM AAA LM-039 M'HAMILTON 20 0 757 1 0 3.8 1 . 8 LEITRIM A LM-O4O 6LENFARN 20 0 364 0 0 8.5 4 . 5 LEITRIM A LM-041 GLENFARN 20 0 549 0 0 4.2 2. 0 LEITRIM AAA LM-042 GLENFARN 20 0 540 0 0 3.8 1 .8 LEITRIM AAA LM-043 GLENEARN 20 0 429 0 0 6.6 3. 0 LEITRIM A LM-044 GLENFARN 20 0 318 0 0 9.4 5. 2 LEITRIM AAA LM-045 LURGANBOY 20 0 287 0 0 9.9 5.2 LEITRIM AAA LM-046 LURGAHBOY 20 0 1022 9 o 1.6 0.4 LEITRIM AAA LM-047 LURGANBOY 20 0 287 0 0 10.2 5.8 LEITRIM AAA LM-048 LURGANBOY 20 0 829 6 0 2.6 0.6 LEITRIM A LM-049 LURGANBOY 20 0 952 1 0 3.3 1 . 6 LEITRIM AAA LM-050 GLENADE 20 429 1306 15 4 0.9 -0.8 LEITRIM AAA LM-051 GLENADE 21 0 345 0 0 9.4 5. 1 LEITRIM AAA LM-O52 GLENABE 20 0 923 0 2.8 1 . 1 LEITRIM AAA LM-053 GLENABE 20 0 569 0 0 7.0 3.5 LEITRIM AAA LM-054 GLENABE 20 0 195 0 0 14.8 8.6 LEITRIM AAA LM-055 AGHALATEEVE 20 0 243 0 0 12.7 7. 5 LEITRIM AAA LM-056 AGHALATEEVE 20 0 352 0 0 8.6 4.8 LEITRIM AAA LM-057 AGHALATEEVE 20 0 357 0 0 9.1 5. 1 LEITRIM AAA LM-058 AGHALATEEVE 20 0 612 1 0 4.5 1 .8 LEITRIM AAA LM-059 AGHALATEEVE 18 0 583 0 0 4.8 2.4 LEITRIM AA LM-060 AGHAVOGHIL 20 0 <100 0 0 ERR ERR LEITRIM AA LM-061 AGHAVOGHIL 20 0 231 0 0 13.5 7.7 LEITRIM AA LM-062 AGHAVOGHIL 20 0 <100 0 0 ERR ERR LEITRIM AAA LM-063 AGHAVOGHH 20 0 •a oo 0 0 ERR ERR LEITRIM AA LM-064 AGHAVOGHIL 20 0 <100 0 0 ERR ERR RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S D . E.B . HO. OF SHEEP MIN MAX 600 Bq/Ks 1000 Bq/K9 K-1000 K-600 LEITRIM LM-065 GLENANIFF 20 200 1140 4 1 2.6 O.t LEITRIM kkk LM-066 GLENANIFF 20 677 1063 20 2 1.3 ~ 2 • n LEITRIM kkk LM-067 GLENANIFF 17 116 786 3 0 3.2 1 . 1 LEITRIM LM-068 GLENANIFF 20 0 795 2 0 3.4 1 . 4 LEITRIM LM-069 GLENANIFF 20 229 1480 18 3 0.6 -0.8 LEITRIM LM-070 YUGAN 20 0 142 0 0 24.2 13.7 LEITRIM kkk LM-071 YUGAN 20 239 1434 17 5 0.7 -0 .7 LEITRIM kkk LM-072 YUGAN 20 0 656 1 0 5.0 2 . 5 LEITRIM k LM-073 YUGAN 11 0 477 0 0 5.4 2. 9 LEITRIM LM-074 YUGAN 20 195 1251 16 6 0.5 -0. B LEITRIM kkk LM-075 DRUMREILLY E. 20 125 398 0 0 8.2 4 . 0 LEITRIM LM-076 DRUMREILLY E. 20 417 1229 17 2 : .0 -1.0 LEITRIM LM-077 DRUMREILLY E. 20 0 1395 17 7 0.4 -0.7 LEITRIM LM-078 DRUMREILLY E. 20 0 1024 11 1 1 .7 -0. 1 LEITRIM LM-079 DRUMREILLY E. 20 174 1181 4 1 2.5 0, 7 LEITRIM kkk LM-080 DRUMREILLY U. 20 0 942 5 0 2.4 0. 5 LEITRIM LM-081 DRUMREILLY U. 20 540 1574 17 4 0.6 -1 .1 LEITRIM LM-082 DRUMREILLY U. 20 280 641 0 5.1 1 . 4 LEITRIM LM-083 DRUMREILLY U. 20 147 863 4 0 3.1 1 .0 LEITRIM LM-084 DRUMREILLY U. 20 0 366 0 0 14.0 7. 0 I..EITRIM LM-085 BARNAMEENAGH 20 0 287 0 0 11.7 6.3 LEITRIM LM-086 BARNAMEENAGH 20 0 429 0 0 8.2 4. 7 LEITRIM LM-087 BARNAMEENAGH 20 308 1323 17 4 0.6 -1 . 1 LEITRIM kkk LM-088 BARNAMEENAGH 20 0 612 1 0 5.0 2.5 LEITRIM LM-089 BARNAMEENAGH 20 0 289 0 0 V3.3 7.7 LEITRIM LM-090 SIRALONGFORD 20 0 1263 12 5 0.7 -0.2 LEITRIM LM-091 STRALONGFORD 20 176 853 5 0 2.7 0.7 LEITRIM LM-092 STRALONGFORB 20 0 316 0 0 10.8 5.13 LEITRIM LM-093 STRALONGFORD 20 501 1159 17 3 1.2 -1 .2 LEITRIM LM-094 STRALONGFORD 20 0 957 6 0 2.2 0.5 CAVAN k CN-001 TIRCAHAN 16 0 <100 0 0 ERR ERR CAVAN kkk CN-002 TIRCAHAN 25 246 694 5 0 4.2 0.9 CAVAN k CN-003 TIRCAHAN 20 0 <100 0 0 ERR ERR CAVAN k CN-004 TIRCAHAN 20 0 443 0 0 9.0 5.2 CAVAN kkk CN-005 BAUNBOY 15 120 283 0 0 15.7 7.9 CAVAN k CN-006 BAUNBOY 20 0 <100 0 0 ERR ERR CAVAN k CN-007 BAUNBOY 20 0 101 0 0 31.2 18.4 CAVAN kk CN-008 BAUNBOY 20 0 163 0 0 23.7 13.8 CAVAN kkk CN-009 BAUNBOY 20 0 166 0 0 26.6 15.8 CAVAN kkk CN-O1O SUANLINBAR 20 0 521 0 0 5.5 2.4 CAVAN kkk CN-O11 SUANLINBAR 18 0 550 0 0 5.7 3.2 CAVAN CN-012 SUANLINBAR 24 457 1175 20 3 1.3 -0.9 CAVAN kkk CN-013 SUANLINBAR 16 152 531 0 0 6.3 2.7 CAVAN kkk CN-014 SUANLINBAR 20 0 358 0 0 10.9 5.4 RANGE ANIMALS OVER COUNTY FLAG HARM NO.'S [i. E. D . NO. OF SHEEP MIN MAX 600 Bq/Kg 1000 Bq/Kg K-1000 K-&00 CAVAN AAA CN-015 KINAULEY 21 144 1391 16 7 0 .5 -0.6 CAVAN AAA CN-016 KINAULEY 19 0 670 2 0 4 .3 I .& CAVAN AAA CN-017 KINAULEY 20 491 991 16 0 1 -B -0.9 CAVAN AAA CN-018 KINAULEY 20 160 764 0 3 .7 1.2 CAVAN CN-019 KINAULEY 20 0 283 0 0 11 .3 7.3 CAVAN AAA CN-020 PEtiRAVOHERS 21 125 745 5 0 2 .9 1 .0 CAVAN AAA CN-021 PEDRAVOHERS 20 0 1023 2 1 3 .0 1.4 CAVAN CN-022 PEtiRAVOHERS 20 198 537 0 0 6 .8 2 .7 CAVAN AAA CN-O23 PEtiRAVOHERS 20 489 854 14 0 3 .4 -0.7 CAVAN AA CN-024 PEDRAVOHERS 20 163 943 8 0 . 1 0.3 CAVAN A CN-025 BENBRACK 20 0 224 0 0 12 .9 7.3 CAVAN AAA CN-026 BENBRACK 20 109 1095 8 2 1.5 O.O CAVAN AAA CN-027 BENBRACK 20 13& 959 14 0 1.5 -0.3 CAVAN AAA CN-028 BENBRACK 24 550 177S 23 16 -0 .3 -1.8 CAVAN AAA CN-029 BENBRACK 20 101 553 0 0 4 • 5 1.9 CAVAN A CN-030 HERRYNANTA 20 0 299 0 0 11 .9 6.5 CAVAN A CN-031 DERRYNANTA 20 0 206 0 0 19 .2 11.4 CAVAN A CN-032 DERRYNANTA 20 0 689 1 0 3 .9 1 .9 CAVAN AAA CN-033 DERRYNANIA 20 0 884 4 0 .4 0.8 CAVAN AAA CN-031 DERRYNANTA 20 662 1442 20 12 -0 .3 -2.1 CAVAN A CN-035 HUNMAKEEVER 20 0 579 0 0 4 .6 2.1 CAVAN A CN-036 DUNMAKEEVER 20 0 339 0 0 B.8 4.6 CAVAN AAA CN-037 DUNMAKEEVER 20 0 854 & 0 .5 0.7 CAVAN A CN-038 DUNHAKEEVER 20 0 254 0 0 15 .8 9.3 CAVAN A CN-039 DUNHAKEEVER 20 109 446 0 0 5 .9 2.6 CAVAN AAA CN-040 DOURA 20 131 884 6 0 .9 0.6 CAVAN AAA CN-041 DOURA 20 326 1247 15 4 0 .8 -0.7 CAVAN A CN-042 DOURA 20 0 441 0 0 8 .3 4.7 CAVAN AAA CN-043 DOURA 20 134 993 7 0 2.2 0.3 CAVAN AAA CN-044 DOURA 20 142 1036 7 1 2 .0 0.4 CAVAN AAA CN-045 HERRYLAHAN 20 168 654 1 0 5 .0 1 .4 CAVAN A CN-046 DERRYLAHAN 20 171 817 0 3 .1 0.9 CAVAN AAA CN-047 DERRYLAHAN 20 438 1300 8 1 2 .0 -0.1 CAVAN AAA CN-048 HERRYLAHAN 24 208 1324 10 3 1.3 -0. 1 CAVAN A CN-049 DERRYLAHAN 20 0 638 1 0 .0 2.4 CAVAN AAA CN-050 TOAM 23 491 1071 19 2 1.7 -1.0 CAVAN AAA CN-051 TOAH 20 278 673 3 0 4 .9 1 .1 CAVAN CN-052 TOAM 21 360 951 17 0 *>.3 -0.8 CAVAN A CN-053 TOAM 20 0 117 0 0 26 • 5 15.5 CAVAN A CN-054 TOAM 20 0 136 0 0 23 .i 13.5 CAVAN AAA CN-055 TEEBANE 21 0 884 3 0 2 .9 1.4 CAVAN AAA CN-056 TEEBANE 23 238 1135 13 3 1.4 -0.2 CAVAN AAA CN-057 TEEBANE 20 443 1055 15 1 1 .8 -0.8 CAVAN AAA CN-058 TEEBANE 21 497 1097 18 1 -1.2 CAVAN AAAA CN-0S9 KILLINAGH 20 134 475 0 C 7 .6 3.5 CAVAN AAA CN-060 KILLINAGH 23 131 595 0 '. 5.1 1.7 CAVAN AAA CN-061 KILLINAGH 20 0 638 2 0 3 .3 1 .0 RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S H. E . H . NO. OF SHEEP MIN MAX 600 Bq/K3 1000 Bq/Ks K-1000 K-600 CAVAN A** CN-062 KILLINAGH 20 240 780 6 0 3.2 0.6 CAVAN AAAA CN-063 KILLINAGH 20 0 230 6 0 15. 1 8. 2 CAVAN A CN-064 ESKEY 20 0 155 0 0 23.1 13.2 CAVAN AA CN-065 ESKEY 20 0 144 0 0 28.3 16.8 CAVAN AAAA CN-066 ESKEY 17 117 371 0 0 10.5 5. 1 CAVAN AAAA CN-067 ESKEY 20 0 227 0 0 18.6 10.8 CAVAN AAAA CN-068 ESKEY 20 0 240 0 0 17.0 9.3 ROSCOMMON A RN-OO1 KEAHUE 14 0 •aoo 0 0 ERR ERR ROSCOMhON A RN-002 KEAIiUE 20 0 295 0 0 12.4 7. 1 RQSCOMMON AAA RN-003 KEABUE 20 0 520 0 0 6.0 3. 2 KOSCOMMON A RN-004 KEADUE 10 0 •aoo 0 0 ERR ERR RQSCOMMON AAA RN-005 KEAIiUE 20 113 559 0 0 6.3 2.9 ROSCOMMON RN-006 ALTAGOULAN 20 257 1513 10 7 0.6 -0 4 ROSCOMMON RN-O07 ALTAGOULAN 19 0 469 0 0 6.9 3.3 ROSCOMMON RN-008 ALTAGCULAN 18 0 503 0 0 6.4 3.3 ROSCOMMON AAAA RN-0O9 ALTAGOWLAN 11 0 413 0 0 5.5 2.9 ROSCOMMON AAAA RN-O1O ALTAGOULAN 20 107 788 4 0 2.9 0.5 ROSCOMMON RN-O11 LOUGH ALLEN 20 0 961 10 0 1 .6 0.3 ROSCOMMON RN-012 LOUGH ALLEN 20 0 1333 14 5 0.8 -0.4 ROSCOMMON RN-013 LOUGH ALLEN 20 0 107 0 0 29.3 17.3 ROSCOMMON A RN-014 LOUGH ALLEN 20 0 •aoo 0 0 ERR ERR ROSCOMMON A RN-O1S BALLYFARNAN 20 0 220 0 0 16.3 9. 6 ROSCOHMON AA RN-016 BALLYFARNAN 20 0 •aoo 0 0 ERfc ERR ROSCOMMON RN-017 BALLYFARNAN 13 257 678 2 0 4.3 1.1 ROSCOMMON + + RN-018 BALLYFARNAN 11 0 aoo 0 0 ERR ERR ROSCOMMON RN-019 BALLYFARNAN 14 0 261 0 0 10.8 6.2 ROSCOMMON + + RN-020 BALLYFARN^N 20 0 -a oo 0 0 ERR ERR ROSCOMMON AA RN-021 BALLYFARNAN 14 0 103 0 0 34.7 20.6 ROSCOMMON A RN-022 AGHAFIN 14 0 <100 0 0 ERR ERR ROSCOMMON RN-023 AGHAFIN 20 0 511 0 0 5.2 2.5 ROSCOMMON AA RN-024 AGHAFIN 10 11 118 0 0 26.5 15.0 ROSCOMMON AA RN-02S AGHAFIN 20 0 •aoo 0 0 ERR ERR ROSCOMMON AAAA RN-026 AGHAFIN 14 0 •aoo 0 0 ERR ERR ROSCOMMON AA RN-027 CROSSNA 20 0 <100 0 0 ERR ERR ROSCOMMON AA RN-028 CROSSNA 18 0 •aoo 0 0 ERR ERR ROSCOMMON AA RN-029 CROSSNA 10 0 •aoo 0 0 ERR ERR ROSCOMMON AA RN-030 CROSSNA 10 0 •aoo 0 0 ERR ERR KOSCOMMON AA RN-031 CROSSNA 20 0 <100 0 0 ERR ERR ROSCOMMON AA RN-032 BOYLE 11 0 •aoo 0 0 ERR ERR ROSCOMMON A RN-033 BOYLE 20 0 •aoo 0 0 ERR ERR ROSCOMMON A RN-035 BOYLE 7 0 •aoo 0 0 ERR ERR ROSCOMMON AAA RN-036 TIVANAGH 20 0 aoo 0 0 ERR ERR ROSCOMMON + + RN-037 IIUANAGH 12 0 aoo 0 0 ERR ERR ROSCOMMON AA RN-038 TIVANAGH 16 0 •aoo 0 0 ERR ERR RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S D . E . Ii. NO. OF SHEEP MIN MAX 600 B q / K 3 1000 Bq/K3 K-1000 K-600 ROSCOMMON AA RN-039 TIVANAGH 16 0 184 0 0 15.8 9.19 ROSCOMMON AA RN-040 TIVANAGH 14 0 <100 0 0 ERR ERR ROSCOMMON AA RN-041 TIVANAGH 20 0 <100 0 0 ERR ERR ROSCOMMON A RN-O42 BALLYEERMAGLE 20 0 171 0 0 21.1 12.37 KOSCOMMON AA RN-043 CREAGH 15 0 432 5.8 2.95 MAYO MO-001 KILGARVAN 25 0 444 0 8.7 4.1 KAYO MO-002 KILGARVAN 25 0 394 0 8.8 4.4 MAYO MO-003 KILGARVAN 25 0 455 0 6.8 3. 1 MAYO MO-004 KILGARVAN 25 0 691 1 6.9 3.5 MAYO MO-005 KILGARVAN 25 0 794 4.1 1 .8 MAYO MO-006 SALLYMOUNT 25 0 880 8 2.4 0.4 MAYO MO-007 SALLYMOUNT 25 0 559 0 5.6 2.B MAYO AA MO-008 SALLYMOUNT 25 0 163 0 23.6 13.7 MAYO MO-009 SALLYMOUNT 25 0 178 0 15.3 B.B MAYO MO-010 SALLYMOUNT 25 0 519 0 6.2 2.7 MAYO MO-011 AITYMASS E. 25 0 277 0 11.2 6.3 MAYO MO-012 ATTYMASS E. 25 220 1140 20 1 .0 -0.6 MAYO MO-013 ATTYMASS E. 25 0 288 0 11.1 5.8 MAYO MO-014 ATTYMASS E. 25 0 387 0 8.0 4. 1 MAYO MO-015 BUNAVEELA 25 0 440 0 8.1 3.8 MAYO MO-016 BUNAVEELA 25 0 504 0 7.3 3.0 MAYO MO-017 BUNAVEELA 25 108 502 0 5.9 2.4 MAYO MO-018 BUNAVEEl.ft 25 207 598 0 7.2 2.8 MAYO A MO-019 BUNAVEELA 25 0 469 0 7.3 3.5 MAYO AAA MO-020 GLENCO 25 0 238 0 li.l 7. 1 MAYO MO-021 GLENCO 25 0 205 0 15.8 8.7 MAYO AAA MO-022 GLENCO 25 0 449 0 5.7 2.6 MAYO MO-023 GLENCO 25 0 528 0 7.4 3.7 MAYO AAA MO-024 GLENCO 25 0 535 0 5.2 2.1 MAYO AAA MO-025 SHESKIN 25 0 191 0 23.7 13.1 MAYO MO-026 SHESKIN 25 0 636 2 4.4 2.0 MAYO AAA MO-027 SHESKIN 25 0 117 0 30.4 17.9 MAYO AAA MO-028 SHESKIN 25 150 645 1 4.7 1.6 MAYO MO-029 KNOCKNALOUER 25 293 704 1 5.1 1.5 MAYO MO-030 KNOCKNALOUEK 25 0 266 0 13.3 7.2 MAYO AAA MO-031 KNOCKNALOUER 25 0 198 0 15.5 8.7 HAYO MO-032 KNOCKNALOUER 25 0 191 0 16.0 9.1 MAYO AAA MO-033 KNOCKNALOUER 25 0 117 0 40.4 24.2 MAYO AAA MO-034 KERRY 25 227 818 2 3.7 1 .0 MAYO AAA MO-035 PERRY 25 0 381 0 8.5 4. 4 MAYO MO-036 KERRY 25 0 334 0 11.5 5.8 MAYO AAA MO-037 KERRY 25 0 295 0 10.7 5.9 MAYO MO-038 KERRY 25 0 345 0 10.5 5.4 MAYO A MO-039 BALLYCASTLE 25 0 <100 0 ERR ERR RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S P.E.D. NO. OF SHEEP MIN MAX 600 Bq/K9 1000 Bq/K9 K-1000 K-600 MAYO A MO-040 BALLYCASTLE 11 0 <100 0 0 ERR ERR MAYO AAA MO-041 BALLYCASTLE 23 0 605 1 0 3.9 1 .6 MAYO A MO-042 BALLYCASTLE 14 0 180 0 0 18.4 10.8 MAYO AAA MO-043 MUINGS 25 0 264 0 0 18.9 9.8 MAYO AAA MO-044 MUINGS 25 0 134 0 0 25.6 14.8 MAYO HO-045 MUINGS 25 0 295 0 0 14.6 7.5 ,MAYO HO-046 MUINGS 25 0 297 0 0 13.0 6.8 MAYO A MO-047 ATTYMASS W. 25 0 <100 0 0 ERR ERR MAYO A M0-04B ATTYMASS U. 25 0 290 0 0 9.6 5.2 MAYO AAA MO-049 BALLYOVEY 25 128 311 0 0 16.2 7.9 MAYO A MO-050 BALLYOVEY 25 0 <100 0 0 ERR ERR MAYO A MO-O51 BALLYOVEY 25 0 292 0 0 11.2 6.2 c e MAYO AAA MO-052 BALLYOVEY 25 0 357 0 0 10.5 •J t J MAYO MO-053 SRAHMORE 25 0 191 0 0 20.8 12.3 MAYO AAA MO-054 SRAHMORE 25 0 447 0 0 7.3 3.8 MAYO A MO-055 SRAHMORE 25 0 162 0 0 20.8 12. 1 MAYO MO-056 SRAHMORE 25 284 693 1 0 6.3 2. 1 MAYO MO-057 SRAHMORE 25 0 563 0 0 7.0 3.1 GALUAY AAA G-OO1 LETTERBRICKAUN 25 0 302 0 0 12.9 7.0 GALUAY A G-002 LETTERBRICKAUN 23 0 227 0 0 12.2 6.8 GALUAY AAA G-003 LETTERBRICKAUN 25 0 349 0 0 9.1 5.0 GALUAY AAA G-004 LETTERBRICKAUN 25 0 116 0 0 28.0 16.2 GALUAY A G-005 LETTERBRICKAUN 25 0 330 0 0 12.7 7.2 GALUAY A G-006 KILLANNIN 25 0 307 0 0 14.3 7.C1 GALUAY AAA G-007 KILLANNIN 25 321 529 0 0 9.4 3.0 GALUAY AAA G-008 KIL1.ANNIN 24 197 586 0 0 5.7 2. 3 GALUAY AAA G-009 KILLANNIN 25 0 781 4 0 2.7 0.9 GALUAY AAA G-O1O KILLANNIN 22 302 788 5 0 3.5 0.7 GALUAY AAA G-011 ILLION 25 0 189 0 0 15.8 8.9 GALUAY AAA G-012 ILLION 25 0 437 0 0 6.8 3.: GALUAY AAA G-013 ILLION 25 141 374 0 0 11.0 5.3 GALUAY AAA G-O14 ILLION 25 183 506 0 0 7.3 2.7 GALUAY AAA G-015 ILLION 25 0 670 1 0 3.9 1.4 GALUAY A G-016 CAMUS 18 0 460 0 0 6.7 3.a GALUAY AAA G-017 CAMUS 25 0 462 0 0 7.6 3.6 GALUAY AAA G-018 CAMUS 22 0 523 0 0 5.0 2.3 GALUAY AAA G-019 CAMUS 25 0 462 0 0 6. 1 3. 1 GALUAY AAA G-020 CAMUS 25 0 760 4 0 3.1 1 .1 GALUAY AAA G-O21 KNOCKBOY 25 0 575 0 0 4.9 2.5 GALUAY AAA G-022 KNOCKBOY 25 0 <100 0 0 ERR ERR GALUAY A G-023 KNOCKBOY 25 0 435 0 0 5.8 2.9 GM.UAY A G-024 KNOCKBOY 25 0 265 0 0 11.1 6.2 GALUAY A G-025 KNOCKBOY 25 0 410 0 0 5.3 2.8 RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S D.E.D. NO. OF SHEEP MIN MAX 600 Bq/Kg 1000 Bq/Kg K-1000 K-600 GALWAY AAA G-026 LOUGHAIClRICK 18 0 397 0 0 9.4 5. 1 GALWAY AAA G-027 LOUGHATORICK 24 0 460 0 0 5.9 2. 8 GALWAY AAA G-028 COOS 19 208 550 0 0 7.1 2.6 GALUAY AAA G-029 COOS 25 0 195 0 0 22. 1 12.9 GALUAY A G-030 COOS 25 0 160 0 0 28.5 16.1 GALWAY AA G-031 HRUMMIN 25 0 <100 0 0 ERF ERR GALUAY AA G-032 HRUMMIN 25 0 <100 0 0 ERR ERR GALWAY A G-033 DRUHHIN 24 0 <100 0 0 ERR ERR GALUAY AA G-034 DRUMMIN 25 0 <100 0 0 ERR ERR GALWAY AA G-035 DRUMMJN 21 0 •a oo 0 0 ERR ERR GrtLUAY AAA G-036 DRUMHIN 23 0 525 0 0 8.1 4. 1 GALUAY AA G-037 DRUMMIN 25 0 139 0 0 19.6 11.4 CLARE A CE-001 DRUMMAAN 25 0 166 0 0 21 .2 12.3 CLARE A CE-002 DRUMMAAN 25 0 aoo 0 0 ERR ERR CLARE A CE-003 DRUMMAAN 25 0 <100 0 0 ERR ERR CLARE A CE-004 INISHCALTRA 22 0 aoo 0 0 ERR ERR CLARE A CE-005 INISHCALTRA 25 0 181 0 0 14.9 8.6 CLARE AA;s CE-006 INISHCALTRA 20 0 216 0 0 18.7 10.6 CLARE A CE-007 INISHCALTRA 25 0 •aoo 0 0 ERR ERR CLARE A CE-008 INISHCALTRA 20 0 •aoo 0 0 ERR ERR CLARE A CE-009 MOUNTSHANNON 20 0 445 0 0 7.9 3.8 00 CLARE A CE-010 MOUNTSHANNON 25 0 •aoo 0 0 ERR ERR CLARE AAA CE-011 MOUNTSHANNON 20 0 248 0 0 12.0 6.8 CLARE AAA CE-012 HOUNTSHANNON 25 0 •aoo 0 0 ERR ERR CLARE AAA CE-013 MOUNTSHANNON 25 0 202 0 0 14.4 8.3 CLARE CE-014 CLOONUSKER 20 256 867 1 0 4.7 1 .3 CLARE A CE-015 CLOONUSKER 25 0 <100 0 0 ERR ERR CLARE A CE-016 CLOONUSKER 20 0 •aoo 0 0 ERR ERR CLARE A CE-017 CLOONUSKER 20 0 103 0 0 36.4 21.7 CLARE A CE-018 CLOONUSKER 20 0 •aoo 0 0 ERR ERR CLARE A CE-019 CAPPAGHABAUN 24 0 179 0 0 19.5 11.5 CLARE A CE-020 CAPPAGHABAUN 20 0 aoo 0 0 ERR ERR CLARE A CE-021 CAPPAGHABAUN 25 j 155 0 0 18.9 11.0 CLARE A CE-022 CAPPAGHABAUN 25 0 •aoo 0 0 ERR ERR CLARE A CE-023 CAPPAGHABAUN 23 0 120 0 0 31 .4 18.7 CLARE A CE-024 KILLANENA 25 0 <100 0 0 ERR ERR CLARE A CE-025 KILLANENA 25 0 < 100 0 0 ERR ERR CLARE A CE-026 KILLANENA 25 0 <100 0 0 ERR ERR CLARE A CE-027 KILLANENA 25 0 <100 0 0 ERR ERR CLARE A CE-028 KILLANENA 25 0 aoo 0 0 ERR ERR KERRY AAA KY-001 BOOLTEENS 24 393 9.5 RANGE ANIMALS OVER COUNTY TLAG FARM NO.'S D.E.D. NO. OF SHEEP MIN MAX 600 Bq/K3 looo bqyy.'j K-1000 K -COO KERRY A KY-002 BOOLTEENS 20 0 168 0 0 21.0 11.7 KERRY AAAA KY-003 BOOLTEENS 20 0 168 0 0 17.9 10.3 •-"• "1 KERRY AAAA KY-004 BOOLTEENS 20 0 266 0 0 9.3 •J • — KERRY AAAA KY-005 BOOLTEENS 20 0 227 0 0 11.4 6.3 KERRY AAAA KY-006 KILGARYLANtiER 20 0 199 0 0 14.3 8.0 KERRY AAA KY-007 KILGARYLANDER 25 0 243 0 0 14.8 7 . ? KERRY KY-008 KILGARYLANtiER 20 190 497 0 0 7.4 3.0 KERRY KY-009 KILGARYLANtiER 20 0 445 0 0 8.5 4 . 1 KERRY KY-O1O KILGARYLANDER 22 0 441 0 0 6.0 3.0 KERRY AAAA KY-O11 LACK 23 0 253 0 0 11.6 KERRY AAAA KY-012 LACK 24 0 210 0 0 12.2 6!e KERRY AAAA KY-013 LACK 24 0 192 0 0 20.0 li.: KERRY AAAA KY-014 LACK 22 0 134 0 0 24.4 14.3 KERRY AAAA KY-015 LACK 21 0 536 0 0 6.9 3. 3 KERRY AA KY-016 INCH 19 0 104 0 0 34.2 20.4 KERRY AAAA KY-017 INCH 21 0 395 0 0 9.5 4.6 KERRY AAAA KY-018 INCH 25 0 173 0 0 16.5 9.6 KERRY AAAA KY-019 INCH 23 0 305 0 0 10.2 5. 4 KERRY AAAA KY-020 INCH 23 0 348 0 0 10.5 6.0 KERRY AAAA KY-O21 BALLINVOHER 24 0 415 0 0 9.4 5. 0 KERRY AAAA KY-022 BALLINVOHER 20 0 495 0 0 6. 1 3 . 2 KERRY AAAA ICY-023 HALLINVOHER 1*1 0 225 0 0 14.7 8. 1 KERRY AAAA KY-024 BALLINVOHER 23 0 <100 0 0 EKR EM KERRY AAAA KY-025 BALLINVOHER 22 0 426 0 0 7.5 3. I KERRY AAAA KY-O26 BALLINACOURTY 22 0 214 0 0 13.8 7.9 KERRY AAAA KY-027 BALLINACOURTY 23 0 426 0 0 6.9 3.: KERRY AAAA KY-028 BALLINACOURTY 24 0 343 0 0 7.2 3.7 KERRY AAAA KY-029 BALUNACOURTY 23 0 363 0 0 10.0 5. :J KERRY AAAA KY-030 BALLINACOURTY 24 0 <100 0 0 ERR EfK KERRY AA KY-031 MINARD 23 0 140 0 0 24.8 1 4 . t KERRY AA KY-032 MINARD 23 0 29*^ 0 0 13.9 8 . 2 KERRY AA KY-033 MINARD 23 0 <100 0 0 ERR EM* KERRY AAAAA KY-034 MINARD in 0 134 0 0 18.7 10.6 KERRY AAAA KY-035 MINARti 23 0 - 100 0 0 EKK Efct< KERRY AAAA KY-036 KINARD 23 0 136 0 0 29.8 16.9 KERRY AAAA KY-037 KINARD 0 171 0 0 20.5 11 ,B KERRY AAAA KY-038 KINARD 23 0 324 0 0 15.5 8.6 KERRY AAAA KY-039 KINARD 23 0 205 0 0 19.7 10.7 KERRY AAAA KY-O4O KINARD 21 0 197 0 20.0 11.0 KERRY AAAA KY-O41 GLIN 20 0 154 0 29.4 16.4 KERRY AAAA KY-042 GLIN 20 0 180 0 0 20.6 11.4 KERRY AAAA KY-043 GLIN 15 0 141 0 0 26.7 15.6 KERRY AAAA KY-044 GLIN 20 0 210 0 0 21 .6 11.5 KERRY AAAA KY-045 GLIN 23 0 219 0 0 17.7 9. < KERRY KY-046 GLANLEE 24 0 195 0 0 15.4 8. ? KERRY KY-047 GLANLEE 25 0 423 0 0 0.9 4. 5 KERRY KY-O48 GLANLEE 25 1B2 495 0 0 7.4 3.0 RANGE AN IMALS OVER COUNTY FLAG rARrt NO.'S D . E . 6 . NO. OF SHEEP MIN MAX 600 t->q /1:3 1000 l KERRY KY-049 GLANLF.E 24 0 276 0 0 11.2 C . 0 KERRY A KY-050 GLANLOUGH 25 12G 425 0 0 10. 1 1 . 7 KERRY A KY-O51 GLANLOUGH 25 0 352 0 0 10.3 Z. 6 KERRY A KY-052 GLANLOUGH 25 119 397 0 0 9.9 '. . G KERRY AAA KY-053 GLANLOUGH 25 382 783 6 0 4.0 ] . 0 KERRY AAA KY-054 GLANLOUGH 161 527 0 0 6. 3 - . •$ KERRY A KY-055 KILGARVAN 25 0 •100 0 0 EHi I:M< KERRY A KY-056 KILGARVAN 25 0 362 0 0 10.6 KERRY AA KY-057 KILGARVAN 24 0 764 0 4 .5 2 . -1 KERRY A KILGARVAN 0 347 KY-058 0 0 14.5 •'. * KERRY AAA KY-059 KILGARVAN 24 0 534 0 0 5.9 2 . (, KERRY AAA KY-065 E'ANAUN 23 0 647 1 0 5.5 KERRY AAA KY-066 HANAUM J3 0 156 0 0 18.1 1 0 . 3 KERRY AAA l'Y-067 F'ANAUN 25 0 1 19 0 0 27. 4 16.1 KERRY AAA KY-068 &ANAUN 24 0 488 0 0 8. 1 2 . '1 KERRY AAA KY-069 &ANAUN 25 0 258 0 0 15.5 e.: KERRY AAA KY-070 GLANMORE 22 0 202 0 0 19. 1 10.4 KERRY AAA KY-071 GLANMORE 24 0 •100 0 0 EM- KM. KERRY AAA KY-072 GLANMORE 23 0 215 0 0 16.9 KERRY AAA KY-073 GLANMORE 24 0 577 0 0 6.-: ~. _ -> KERRY + * KY-O74 GLANMORE 23 0 104 0 0 26. 1 ; r,. 3 KERRY AAA KY-075 ARPEA 2 3 0 219 0 0 11.8 C E R R Y AAA KY-076 t-.RPEA 21 0 278 0 0 12.4 6.6 KERRY AAA KY-077 ARPEA 20 0 165 0 0 16.7 n r KERRY + > KY-078 ARPEA 19 0 358 0 0 11.7 ;.•. i KERRY AAA KY-079 ARPEA 23 0 286 0 0 12.3 (. •} KERRY AAA KY-080 PAUROS 24 0 538 0 0 6.3 2 . <: KERRY AAA KY-081 PAUROS 24 0 304 0 0 10.9 r _ -1 KERRY AAA KY-082 PAUROS 24 0 193 0 0 13.0 7 . ? KERRY AAA KY-083 DAUROS 24 0 219 0 0 12.9 ". 0 KERRY AAA KY-084 PAUROS 25 0 323 0 0 10.1 KERRY AAA KY-085 KENMARE 21 0 304 0 0 8.7 4. 8 KERRY AAA KY-086 KENMARE 23 0 208 0 0 13.3 "* . 3 KERRY AAA KY-087 KENMARE 23 0 332 0 0 8.7 4 . •> KERRY AAA KY-088 KENMARE 25 0 369 0 0 9.0 4.8 KERRY AAA KY-089 REEN 25 0 393 0 0 8.9 4 . t KERRY AAA KY-090 REEN 25 0 189 0 0 20 .9 12.3 KERRY AAA KY-091 REEN 25 0 334 0 0 11.8 t . 2 KERRY AAA KY-092 REEN 25 1 19 369 0 0 12.5 ' . 7 KERRY AA KY-093 GREENANE 23 0 115 0 0 29.2 17.1 KERRY AAA KY-094 PROMORE 25 0 2S8 0 0 12.1 6, e KERRY AAA KY-095 DROMORE 20 161 332 0 0 16.1 7.{, KERRY AAA KY-096 PROMORE 24 0 417 0 0 10.0 Z. 4 KERRY AAA KY-097 PROMORE 21 0 276 0 0 14.9 7 . "* KERRY AA KY-098 DROMORE 25 0 1B4 0 0 18.6 10.3 KERRY AAA KY-099 LOUGH&RIN 25 0 304 0 0 9.7 4 . " RANGE ANIMALS OVER CnUNTY FLAG FARM NO.'S 0 . E . [i. NO. OF SHEEP MIN MAX 600 1000 K-1000 K - 60 10UGHPRIN KERRY AAA KY-099 25 0 364 0 9.7 -0 KERRY AAA KY-1OO LOUGHBRIN **5 0 233 0 13.0 6 KERRY AAA KY-101 LOUGHBRIN 24 0 404 0 10.0 . 0 KERRY ie AAA KY-102 LOUGHBRIN 124 434 0 10.B •j .0 KERRY AAA KY-103 LOUGHBRIN 25 0 187 0 16.5 <), /, KERRY AAA KY-104 TAHILLA 25 0 171 0 21 .1 1 2 3 KERRY AAA KY-105 TAHILLA 24 0 278 0 11.9 6 .7 KERRY AAA KY-1OG TAHILLA 20 0 234 0 15.1 7 . fi KERRY AAA KY-107 TAHILLA 20 0 3 30 0 11.7 .8 KERRY AAA KY-1OB TAHILLA 24 0 2 17 0 16.1 9. 0 KERRY AAA KY-109 SNEEM 25 0 269 0 13.2 7 . 1 KERRY AAA KY-UO SNEEM 20 111 345 0 11 .4 •\. 6 KERRY AA KY-111 SNEEM 25 0 206 0 16.6 9 KERRY AAA KY-112 SNEEM 25 0 219 0 16.4 B. 1! KERRY KY-113 VENTRY 21 0 219 0 16.6 9 .0 KERRY KY-1H VENTRY 20 0 276 0 9.4 . 1 KERRY KY-115 VENTRY 21 0 250 0 16.2 9 . < KERRY KY-116 VENTRY 21 0 117 0 29.3 17 . 3 KERRY KY-117 DUNURLIN 20 0 269 0 13.1 6 KERRY KY-118 DUNURLIN 23 0 167 0 19.6 1 1 . 1 KERRY KY-119 DUNURLIN 20 252 562 0 e.e 3. 1 KERRY KY- 20 DUNURLIN 19 164 «58 0 9.5 3 . 3 KERRY KY- 121 DUNURLIN 20 0 171 0 15.5 e.9 KERRY KY- DUNQUIN 22 0 299 0 13.7 7 . 4 KERRY KY- 23 DUNQUIN 23 0 260 0 1 0 . S 6 . 1 KERRY KY- 24 DUNOUIN 22 0 167 0 10.0 10 . 3 KERRY KY- 25 DUNOUIN 20 0 197 0 16.1 n .0 KERRY KY- 26 DUNQUIN 20 0 213 0 13.4 ? . t KERRY KY-127 DINGLE 0 217 0 15.5 5 . 5 KERRY KY-12B DINGLE 23 0 250 0 13.5 7 . ?. KERRY KY-129 DINGLE 22 0 • 100 0 n ERR EKK KERRY KY-130 DINGLE 2 0 217 0 16. 1 8 -7 KERRY KY-131 DINGLE 19 0 217 0 12.9 •7 . ; KERRY KY-132 MARHIN 21 0 165 0 16.5 .;; KERRY KY-133 MARHIN 22 0 331 0 10.9 KERRY KY-134 MARHIN 21 0 284 0 10.7 5 . KERRY KY-146 KILMALKEDAR 22 0 391 0 0 6.8 3 .'y KERRY KY-147 KILMALKEDAR 24 0 208 0 0 19.2 10.6 KERRY KY-148 KILMALKEPAR 21 0 193 0 0 17.9 l o. r. KERRY KY-149 KILMALKEIiAR 24 0 323 0 0 7.8 3 . 9 KERRY KY-150 KILMALKEDAR 22 0 299 0 0. 13.2 7. 3 KERRY A KY-151 FALLYDUFF 21 0 120 0 0 30.8 10.0 i: i: R R Y AA KY-152 BALLYDUFF 20 0 165 0 0 15.9 9. 1 KERRY KY-153 BALLYDUFF 21 0 <100 0 0 ZhH EfcP KERRY A A KY-154 BALLYDUFF 21 0 <100 0 0 ERh El KERRY AAA KY-239 EMLAGH 25 0 278 0 0 13.2 7.3 KERRY AAA KY-240 EMLAGH 25 0 326 0 0 7.9 4. 1 KERRY AAA KY-241 CAHER 25 0 178 0 0 14.8 8.3 KERRY AAA KY-242 CAHER 25 0 213 0 0 15.4 9. 1 KERRY AAA KY-243 CAHER 25 0 753 1 0 4.6 2.3 KERRY AAA KY-244 CAHER 25 0 137 0 0 23.0 13.3 KERRY AAA KY-245 CAHER 25 0 193 0 0 18.9 10.4 KERRY AAAA KY-246 BALLINSKELLIGS 25 0 571 0 0 5.3 2.1 KERRY AAAA KY-247 BALLINSKELLIGS 25 0 150 0 0 22.3 13.0 KERRY AAA KY-248 BALLINSKELLIGS 24 0 197 0 0 18.3 10.5 KERRY AAA KY-249 BALLINSKELLIGS 25 0 135 0 0 22.7 13.2 KERRY AAA KY-250 BALLINSKELLIGS 22 0 <100 0 0 ERR ERR KERRY AAAA KY-251 BALLINSKELLIGS 25 0 161 0 0 16.7 9.G KERRY AAA KY-252 BALLINSKELLIGS 25 0 295 0 0 13.4 7.3 KERRY AAAA KY-253 BALLINSKELLIGS 25 0 130 0 0 28.3 16.8 KERRY AAA KY-254 MASTERGEEHY 25 0 208 0 0 16.2 9.2 KERRY A KY-255 MASTERGEEHY 20 0 119 0 0 33.6 20.0 KERRY AAA KY-256 MASTERGEEHY 25 0 451 0 0 11.2 5. 7 KERRY AAA KY-257 MASTERGEEHY 25 0 883 2 0 4.4 2.1 KERRY AAA KY-258 MASTERGEEHY 25 0 354 0 0 11.1 5.5 KERRY AAAA KY-259 CAHERDANIEL 20 0 <100 0 0 ERR ERR KERRY AAA KY-260 CAHERBANIEL 25 0 271 0 0 15.7 9.1 KERRY AAA KY-261 CAHERCANIEL 25 0 299 0 0 9.3 5.0 KERRY AAA KY-262 CAHERDANIEL 25 0 197 0 0 16.2 9.5 KERRY AAA KY-263 BAHAGHS 25 0 221 0 0 13.9 7.9 KERRY AAA KY-264 BAHAGHS 24 0 269 0 0 12.1 6.2 KERRY AAA KY-265 BAHAGHS 25 0 414 0 0 10.3 5. 2 KERRY AAA KY-266 BAHAGHS 25 0 254 0 0 13.6 7.3 KERRY AAA KY-267 BAHAGHS 25 0 289 0 0 14.1 7.8 KERRY AAA KY-268 BALLYBRACK 25 0 297 0 0 10.4 5.7 KERRY AAA KY-269 BALLYBRACK 25 0 280 0 0 11.2 6.0 KERRY AAA KY-270 BALLYBRACK 25 0 297 0 0 9.6 5.2 KERRY AAA KY-271 BALLYBRACK 25 0 228 0 0 10.5 5.9 KERRY AAA KY-272 CANUIG 25 0 208 0 0 15.9 8.8 KERRY AAAA KY-273 CANUIG 25 0 156 0 0 16.4 9.5 KERRY AAA KY-274 CANUIG 25 0 267 0 0 15.2 8. 1 KERRY AAAA KY-275 CANUIG 25 0 165 0 0 20.0 11.4 CORK AAA C-001 KILNAMANAGH 20 0 214 0 0 17.1 9.4 CORK AAA C-002 KILNAMANAGH 22 0 302 0 0 11 .0 6.0 CORK AAA C-003 KILNAMANAGH 20 0 242 0 0 12.0 6.7 CORK AAA C-004 KILNAHANAGH 24 0 168 0 0 22.3 13.0 CORK AAA C-005 KILNAMANAGH 20 0 <100 0 0 ERR ERS CORK AAA C-006 COULAGH 20 0 300 0 0 13.0 7.1 CORK AAA C-007 COULAGH 23 0 238 0 0 13.3 7.4 RANBfc ANIMALS OVER COUNTY FLAG FARM NO.'S D . E . D. NO. OF SHEEP MIN MAX 600 6q/K9 1000 Pq/Kg K-1000 K - 6 0 0 CORK A A A C-008 COULAGH 23 0 136 0 0 25.0 14.6 CORK AAA C-009 COULAGH 23 0 147 0 0 20.5 11.9 CORK AAA C-010 COULAGH 23 0 199 0 0 16.8 9.3 CORK AAA C-Oll KILLACONENAGH 22 0 361 0 0 11.8 6. 2 CORK AAA C-O12 KILLACONENAGH 20 0 320 0 0 13.8 6.9 CORK AAA C-013 KILLACONENAGH 21 0 179 C 0 in o 12.3 CORK AAA C-014 KILLACONENAGH 20 0 192 0 0 15.2 8.5 CORK AAA C-015 KILLACONENAGH 20 0 197 0 0 23.8 12.6 CORK AAA C-016 KILCATHERINE 20 0 233 0 0 14.9 7. 9 CORK AAA C-017 KILCATHERINE 22 0 350 0 0 10.4 5. 7 CORK AAA C-018 KILCATHERINE 20 0 289 0 0 13.0 7. 1 CORK AAA C-019 KILCATHERINE 23 0 168 0 0 20.5 11.8 CORK C-020 KILCATHERINE NO SHEEP PRESENTED FOR MEASUREMENT CORK AAA C-021 KILCASKIN 23 0 110 0 0 26.4 15.6 CORK AAA C-022 KILCASKIN 20 0 227 0 0 12.5 6.9 CORK AAA C-023 KILCASKIN 20 0 199 0 0 13.4 7.6 CORK AAA C-024 KILCASKIN 21 0 164 0 0 23.5 13.8 CORK AAA C-025 KILCASKIN 23 0 175 0 0 20.5 11 . 5 CORK A*A C-026 KILCASKIN 20 0 246 0 0 16.6 9.0 CORK AAA C-027 KILCASKIN nn 0 233 0 0 14.2 7. 8 CORK AAA C-028 KILCASKIN 20 127 328 0 0 13.2 6.4 CORK AAA C-029 KILCASKIN 20 0 <100 0 0 ERR ERR CORK AAA C-030 KILCASKIN 20 0 197 0 0 17.8 9.8 CORK AAA C-031 AHIL 25 0 225 0 0 19.8 10.6 CORK AAA C-032 AHIL 20 0 305 0 0 11.5 5.8 CORK AAA C-033 AHIL 20 0 127 0 0 27.1 15. 6 CORK C-034 AHIL NO SHEEP PRESENTED FOR MEASUREMENT CORK AAA C-035 AHIL 22 0 231 0 0 13.9 7. S3 CORK AAA C-036 DOUCE 24 0 192 0 0 16.2 9. 2 CORK AAA C-O3? DOUCE 22 0 112 0 0 26.3 15. 4 CORK AAA C-038 DOUCE 20 0 235 0 0 15.0 8.2 CORK AAA C-039 DOUCE 20 0 268 0 0 11.4 6.2 CORK AAA C-040 IiOUCE 20 0 324 0 0 11.1 5.7 CORK AAA C-041 KEALKIL 20 0 114 0 0 24.5 14,2 CORK AAA C-042 KEALKIL 20 0 361 0 0 11.0 5.8 CORK AAA C-043 KEALKIL 25 143 408 0 0 9.4 4 .4 CORK AAA C-044 KEALKIL 20 0 393 0 0 8.9 4.4 CORK AAA C-045 KEALKIL 20 0 214 0 0 16.1 8.9 CORK AAA C-O46 MEALAGH 20 0 231 0 0 14.7 8.0 CORK AAA C-047 MEALAGH 23 0 179 0 0 17.1 9.(3 CORK AAA C-048 MEALAGH 20 0 <1CO 0 0 45.6 27.1 CORK AAA C-049 MEALAGH 13 0 112 0 0 30.0 17.6 CORK AAA C-050 MEALAGH 20 0 201 0 0 21.2 12.6 CORK AAA C-051 BANTRY 20 0 <100 0 0 ERR ERR CORK AAA C-052 PANTRY 20 0 •noo 0 0 ERR ERR CORK AAA C-053 BANTRY 20 0 162 0 0 18.8 10.8 CORK AAA C-054 PANTRY 20 0 <:ioo 0 0 ERR ERR RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S D . E . Ii. NO. OF SHEEP HIN MAX 600 Bq/K3 1000 Bq/Kg K-1000 K-60' CORK AAA C-055 PANTRY 20 0 <100 0 0 ERR ERR CORK AAA C-056 BEAR 20 0 168 0 0 16.6 9.5 CORK AAA C-057 BEAR 20 0 283 0 0 15.6 9.3 CORK AAA C-058 BEAR 20 0 102 0 0 30.2 17.9 CORK AAA C-059 BEAR 20 0 186 0 0 16.3 9.3 CORK AAA C-060 BEAR 20 0 253 0 0 14.9 7.8 CORK AAA C-061 DURRUS WEST 20 0 130 0 0 20.7 12.1 CORK AAA C-062 HURRUS WEST 20 0 158 0 0 IS.2 10.5 CORK AAA C-063 DURRUS WEST 20 0 372 0 0 9.7 5.6 CORK AAA C-OS4 DURRUS WEST 20 0 350 0 0 9.7 5. 1 CORK A A.A C-055 DURRUS WEST 20 0 <100 0 0 ERR ERR CORK AAA C-06G GLENLOUGH 20 0 210 0 0 13.5 7.5 CORK AAA C-067 GLENLOUGH 20 0 343 0 0 10.1 5.7 CORK AAA C-068 GLENLOUGH 20 0 201 0 0 14.4 8.2 CORK AAA C-069 GLENLOUGH 20 0 179 0 0 13.5 7.7 CORK AAA C-070 SHEEPS HEAD 12 0 343 0 0 7.1 3.9 CORK AAA C-071 SHEEPS HEAD 20 0 216 0 0 14.6 8.5 CORK AAA C-072 SHEEPS HEAD 20 0 216 0 0 14.2 7. B CORK AAA C-073 HURRUS EAST 20 0 318 0 0 9.9 5.6 CORK AAA C-074 DURRUS EAST 20 0 289 0 0 7.9 4.3 CORK AAA C-075 DURRUS EAST 20 0 376 0 0 8.6 4.2 CORK AAA C-076 DURRUS EAST 20 0 <100 0 0 ERR ERR CORK AAA C-077 DURRUS EAST 20 0 309 0 0 10.9 6.2 CORK AAA C-078 DUNBEACON 20 0 190 0 0 17.0 9.9 CORK AAA C-079 DUNBEACON 20 0 300 0 0 11.4 6. 1 CORK AAA C-080 DUNBEACON 20 0 162 0 0 19.6 11.3 CORK AAA C-O8J DUNPEACON 20 0 207 0 0 15.6 9.0 CORK AAA C-082 DUNBEACON 20 0 166 0 0 17.0 10.0 CORK AAA C-083 PUNMANUS 20 108 337 0 0 12. 0> 6. 1 CORK AAA C-084 BUNMANUS 20 0 143 0 0 25.3 14.9 CORK AAA C-085 DUNMANUS 20 0 179 0 0 16.6 9.4 CORK AAA C-086 PUNMANUS 20 0 233 0 0 14.1 7.7 CORK AAA C-087 SCHULL 20 0 158 0 0 18.5 10.8 CORK AAA C-088 SCHULL 20 0 <100 0 0 ERR ERR CORK AAA C-089 SCHULL 20 0 330 0 0 8.9 4.9 CORK AAA C-090 SCHULL 20 0 <100 0 0 ERR ERR CORK C-091 CURRYGLASS 20 0 281 0 0 13.6 7.3 CORK AAA C-092 CURRYGLASS 20 0 253 0 0 15.7 8.6 CORK C-093 CURRYGLASS 20 166 408 0 0 9.3 4.1 CORK AAA C-094 CURRYGLASS 20 0 <100 0 0 ERR ERR CORK AAA C-095 CURRYGLASS 20 0 134 0 0 25.5 14.9 CORK AAA C-096 GLENGARRIFF 23 0 145 0 0 24.9 14.7 CORK AAA C-097 GLENGARRIFF 23 0 162 0 0 19.6 11.2 CORK AAA C-O98 GLENGARRIFF 20 173 350 0 0 13.5 6.3 CORK AAA C-099 GLENGARRIFF 20 136 311 0 0 14.1 6.9 CORK AAA C-1O0 GLENGARRIFF 20 0 220 0 0 15.4 8.5 CORK AAA C-1O1 BALLYBANE 20 0 222 0 0 13.8 8.0 RANGE ANIMALS OVER COUNTY FLAG FARM NO. 'S D.E.D. NO. OF SHEEP MIN MAX 600 Bq/K3 1000 Bq/Kg K-1000 K-600 CORK kkk C-102 BALLYBANE 20 0 266 0 0 13.3 7.4 CORK kkk C-103 BALLYKANE 20 0 168 0 0 15.9 9.2 CORK kkk C-104 BALLYBANE 20 0 184 0 0 17.2 10.1 CORK kkk C-105 BALLYDEHOB 20 0 184 0 0 17.3 10. 1 CORK kkk C-106 BALLYDEHOB 20 0 300 0 0 10.0 5.7 CORK kkk C-107 BALLYDEHOB 20 0 <100 0 0 ERR ERR CORK kkk C-108 BALLYDEHOB 20 0 235 0 0 13.4 7.8 CORK kkk C-1O9 BALLYDEHOB 20 0 246 0 0 11.1 6.2 CORK kkk C-11O CROOKHAVEN 20 0 194 0 0 12.5 7. 1 CORK kkk C-lll CROOKHAVEN 20 0 210 0 0 13.1 7. 4 CORK kkk C-112 CROOKHAVEN 20 0 130 0 0 31 .6 18.8 CORK kkk C-113 CROOKHAVEN 20 0 179 0 0 18.6 10. 9 CORK kkk C-114 CROOKHAVEN 20 0 322 0 0 11.2 5.7 CORK kkk C-115 GOLEEN 20 0 266 0 0 15.0 8.6 CORK kkk C-116 GOLEEN 20 0 179 0 0 18.5 10.8 CORK kkk C-117 GCLEEN 20 0 175 0 0 15.7 9. 1 CORK kkk C-118 GOLEEN 20 0 127 0 0 23.4 13.7 CORK kkk C-119 GOLEEN 20 0 225 0 0 14.2 8.2 5 UATERFORD UD-OO1 TINNISAGGART 20 250 785 5 0 3.3 0.7 UATERFORD + + un-002 TINNISAGGART 20 0 498 0 0 7.1 3.3 UATERFORD UD-003 TINNISAGGART 20 0 231 0 0 11.2 6.2 WATERFORD UD-004 TINNISAGGART 20 113 811 3 0 3.4 1 . 3 UATERFORD UD-005 TINNISAGGART 25 48 1445 21 14 0.2 -0.8 UATERFORD + + UD-006 CAPPOGUIN 20 0 524 0 0 8.0 4.7 UATERFORD UD-007 CAPPOQUIN 21 491 1316 17 2 1 .2 -0.8 UATERFORD uD-ooa CAPPOQUIN 20 167 779 3 0 3.7 0.9 UATERFORD kkk WD-009 CAPPQGUIN 25 405 1221 19 6 0.8 -0.8 UATERFORD kkk UD-092 CAPPOQUIN 25 326 1203 19 3 1.3 -0.5 UATERFORD UD-010 KNOCK-BRANOAUN 20 0 715 2 0 3.9 1.4 UATERFORD kkk UD-O11 KNOCK-BRANHAUN 20 286 970 7 0 2.0 0.2 UATERFORD kkk UD-012 KNOCK-BRANDAUN 20 0 1243 10 2 1.6 0.1 UATERFORD kkk UD-013 KNOCK-BRANDAUN 36 0 255 0 0 12.0 6.7 UATERFORD kkk UD-014 GRAIGNAGOUER 40 191 711 5 0 4.6 1 .2 UATERFORD kkk uri-015 GRAIGNAGOUER 20 220 1032 9 1 2.0 0. 1 UATERFORD kk UD-016 GRAIGNAGOUER 20 0 321 0 0 9.3 5.0 UATERFORD kk UD-017 GRAIGNAGOUER 7 0 <100 0 0 ERR ERR UATERFORD UD-018 ST-MARYS 20 132 887 7 0 2.2 0.4 UATERFORD UD-019 ST-MARYS 20 422 931 15 0 2.0 -0.6 UATERFORD kkk UD-020 ST-MARYS 20 0 647 1 0 4.8 2.2 UATERFORD UD-021 ST-MARYS 20 317 979 15 0 1.7 -0.9 WATERFORD kkk UD-022 SI-MARYS 5 117 378 0 0 7.4 3.8 UATERFORD kkk UD-023 ST-MARYS 14 167 508 0 0 5.5 2. 1 UATERFORD kkk UD-024 GURTEEN 19 218 807 7 0 2.9 0.5 UATERFORD kkk UD-025 GURTEEN 20 0 249 0 0 14.2 7.6 RANGE ANIMALS OVER COUNTY FLAG FARM NO.'S D.E.D. HO. OF SHEEP MIN MAX 600 Bq/K3 1000 Bq/Kg K-1000 K-600 UrtTERFORP kkk UD-026 GURTEEN 15 0 629 1 0 4.1 1.7 UATERFORH k UD-027 GURTEEN 10 0 304 0 0 13.9 6.9 WATERFORD k UD-028 GURTEEN 10 0 348 0 0 8.5 4.6 WATERFORB k WD-029 GURTEEN 24 605 1650 24 15 -0.3 -1 .6 UATERFORD + + UD-030 FEUS 15 0 220 0 0 11.9 6.6 UATERFORD UD-03I FEUS 8 0 297 0 0 8.0 4. 4 UATERFORD + + UD-032 FEUS 6 0 477 0 0 4.6 1.9 UATEREORD + + UD-033 FEUS 6 0 425 0 0 4.5 2. 1 UATERFORD -t + UD-O34 COURMARAGLIN 9 158 328 0 0 12.8 6.1 UA1ERFORD kk UD-035 COURMARAGLIN 6 0 <100 0 0 ERR ERR UATERFORD kk UD-036 COURMARAGLIN 4 0 211 0 0 10.1 5.5 UATERFORD kk UD-037 COURMARAGLIN 4 0 <100 0 0 ERR ERR UATERFORD kk UD-O38 COURMARAGLIN % 0 147 0 0 12.3 7.0 UATERFORD kk UD-039 COURMARAGLIN & 161 352 0 0 10.3 4.5 UATERFORD + + UD-080 COURMARAGLIN 5 163 312 0 0 12.1 5.6 UATERFORD + + UD-078 COURMARAGLIN 16 0 766 3 0 2.8 1.0 UATERFORD + + WD-O40 BALLYMACARBRY 10 0 178 1 1 13.8 7.9 UATERFORD UD-041 BALLYMACARBRY 25 141 1914 15 7 0.5 -0.4 UATERFORD UD-042 BALLYMACARBRY 25 0 2031 20 14 -0.1 -0.9 UATERFORD kkkk UD-043 BALLYMACARBRY 13 0 1175 3 1.6 0.7 UATERFORD UD-044 BALLYMACARBRY 16 0 1155 5 I 1.8 0.5 UATERFORD kk UD-O45 BALLYMACARBRY 10 0 328 0 0 7.3 3.7 UATERFORD kkk UIi-046 ROSS 21 123 618 1 0 5.1 2.3 UATERFQRD kkk UD-O47 ROSS g 0 1069 1 1 2.3 0.9 UATERFORD kkk UD-048 BALLYSAGGART 13 0 618 2 0 2.9 1.3 UATERFORD k UD-049 BALLYSAGGART 21 264 781 4 0 3.9 0.9 UAIEREORD UD-050 BALLYSAGGART 20 174 1129 12 3 1.2 -0.2 UATERFORD k UD-051 BALLYSAGGART 10 0 458 0 0 4.4 2.3 UATERFORD UD-052 BALLYSAGGART 24 869 2136 24 21 -1.0 -2.3 UATERFORD UD-053 BALLYSAGGART 19 521 1155 17 2 1.1 -1.2 WATERFORD UD-055 BALLYIN 18 693 2996 18 16 -1.2 -1.8 UATERFORD UD-056 BALLYIN 10 836 2622 10 9 -1.5 -2.2 UATERFORD taD-082 BALLYIN 20 682 1848 20 14 -0.8 -2.0 UATERFORD UB-083 BALLYIN 24 0 2339 23 23 -0.8 -1 .7 UATERFORD UD-O84 BALLYIN 21 1100 1762 21 21 -1.6 -3.4 UATERFORD kkk UD-091 BALLYIN 15 106 1100 4 2 1.8 0.6 UATERFORD kkkk UD-092 BALLYIN 17 0 1978 3 3 1.0 0.3 UATERFDRD kk 1-ID-054 BALLYIN 7 0 <100 0 0 ERR ERR UATERFORD kk UO-057 BALLYIN 4 0 <100 0 0 ERR ERR UATERFORD kk UD-085 BALLYIN 4 0 <100 0 0 ERR ERR UATERFORD kk UD-058 BALLYHUFF 7 0 <100 0 0 ERR ERR UATERFORD kk UD-059 BALLYDUFE 5 0 <100 0 0 ERR ERR UATERFORD kk UD-060 BALLYHUFF 6 0 <100 0 0 ERR ERR UATERFORD kk UD-061 BALLYBUFF 4 0 <100 0 0 ERR ERR UAIERFORD kk UD-062 BALLYDUFF 6 0 <100 0 0 ERR ERR UATERFORD kk UD-063 BALLYDUFE 7 0 <100 0 0 ERR ERR UATERFORII k UD-065 RATHGORMACK 9 0 282 0 0 9.5 5.3 XftiNUE ANIMALS OVER COUNTY FLAG FARM NO.'S D . E . D . NO. OF SHEEP MIN MAX 600 Bq/K9 1000 Bq/K3 K-1000 K-600 UrtTERFORD AAA UD-066 RATHGORMACK 14 0 823 3 0 2.9 1 . 1 UATEREORD A UD-067 RATHGORMACK 6 0 139 0 0 17.4 9. 9 UATERFORD A UD-068 RATHGORMACK 9 220 557 0 0 5.7 2 .0 UATERFORD AAA UD-064 COMERAGH 15 0 396 0 0 6.6 3.5 WATERFDRD UD-069 COMERAGH 20 139 1324 10 3 1 .0 -0.2 UATERFORD AAA UD-070 COMERAGH 14 216 684 1 0 4.3 1 . 3 UATERFORD + + UD-071 COMERAGH 16 0 123 0 0 21 .3 12.5 UATERFORD + + UD-072 COMERAGH 15 0 198 0 0 15.8 9 . 3 UATERFORD AAA UD-073 COMERAGH 20 0 328 0 0 12.5 7. 3 UATERFORD + + UD-074 COMERAGH 7 0 125 0 0 23.0 13.0 UATERFORD AAA WD-O75 COMERAGH 18 227 788 11 0 2.7 0.0 UATERFORD UD-079 COURMARAGLIN 25 0 345 0 0 7.0 3. 8 UATERFORD UD-081 COURMARAGLIN 8 535 1104 7 3 0.7 -1 . 4 UATERFORD UD-093 COURMARAGLIN 25 451 1463 17 7 0.6 -0 . 8 UATERFORD A* WD-086 SESKINAN 15 0 612 1 0 5 • 8 3 . 3 UAIERFORD + + UD-087 SESKINAN 14 0 <100 0 0 ERR ERR UATESFORH UIi-088 SESKINAN 20 220 1192 10 4 1.0 -0 . 4 UATERFORD + + WD-O89 SESKINAN 16 0 926 3 0 2.7 1.3 + + WATERFORD UD-090 SESKINAN 20 317 1256 8 1 2.0 0. 1 TIPPERARY TS-OO1 NEUCASTLE 20 139 1077 5 1 2.3 0. 5 TIPPERARY TS-002 NEUCASTLE 20 181 708 2 0 4 .2 1 . 4 TIPPERARY TS-OO3 NEUCASTLE 20 284 924 12 0 2.0 -0 .1 TIPPERARY AA TS-004 NEUCASTLE 20 0 <100 0 0 ERR ERR TIPPERARY TS-005 NEUCASTLE 20 323 916 8 o 2.2 0.1 TIPPERARY AAA TS-O06 CLOGHEEN 35 0 197 0 0 16.5 9.3 TIPPERARY TS-007 CLOGHEEN 35 0 273 0 0 13.0 7. 1 TIPPERARY TS-008 CLOGHEEN 26 0 1701 18 9 0.4 -0.5 TIPPERARY TS-009 CLOGHEEN 22 160 634 1 0 5.7 2. 4 TIPPERARY TS-O1O CLOGHEEN 27 0 1065 9 3 1.6 0.6 TIPPESARY TS-O11 COOLG'ANROE 25 0 768 4 0 3.3 1 .0 TIPPERARY TS-O12 COOLG'ANROE 20 260 587 0 0 6.2 1 .6 TIPPERARY + + TS-013 COOLG'ANROE 25 143 319 0 0 15.4 7. 1 TIPPERARY TS-014 COOLG'ANROE 10 106 418 0 0 6.5 2.9 TIPPERARY TS-015 COOLG'ANROE 20 253 565 0 0 5.8 1 .7 TIPPERARY TS-O16 BURNCOURT 25 0 640 1 0 5.7 2.3 T IPPERARY TS-017 BURNCOURT 25 299 592 0 0 7.4 1.7 TIPPERARY TS-018 BURNCOURT 25 141 858 1 0 4.9 1 .8 TIPPERARY TS-019 BURNCOURT 25 176 563 0 0 6.4 2.5 TIPPERARY TS-020 BURNCOURT 13 0 389 0 0 8.6 4.1 TIPPERARY TS-021 TUBER ID 18 0 345 0 0 8.6 4.(3 TIPPERARY TS-022 KILCOMMON 25 0 389 0 0 8.9 4.6 TIPPERARY TS-O23 KILCOMMON 25 152 682 1 0 5.2 1 .9 TIPPERARY TS-024 TEMPLENEIRY 25 106 1305 15 4 0.9 -0.3 TIPPERARY TS-025 TEMPLENEIRY 25 431 1212 16 3 1.2 -0.5 NtiE ANIMALS OVER COUNTY FLAG FARM NO.'S D. E . n. NO. OF SHEEP MIN MAX 600 Bq/K3 1000 Bq/K9 K-1000 K-600 TIPPERARY TS-026 TEMPLENEIRY 9 0 246 0 0 14.9 7.9 TIPPERARY TS-027 TEMPLENEIRY 21 233 1214 20 6 0.6 -1 . 4 TIPPERARY + + TS-028 TEMPLENEIRY 21 0 759 1 0 4.2 1 .8 TIPPERARY TS-O29 CLONBEG 25 491 1346 24 5 0.9 -1 .'J TIPPERARY IS-030 CLONBEG 25 216 882 8 0 2.4 0.4 TIPPERARY TS-031 CLONBEG 16 238 1087 6 1 2.0 0.3 TIPPERARY TS-032 CLONBEG 12 165 590 0 0 4.2 1 .6 TIPPERARY TS-033 CLONBEG 20 213 906 7 0 2.3 0.5 UEXFORD A UX-001 KILLANN 20 0 117 0 0 32.2 19.2 UEXFORD A UX-002 KILLANN 20 0 143 0 0 30.0 17. 8 WEXFORD AA UX-003 KILLANN 15 0 <100 0 0 ERR ERR UEXFORD AA UX-O04 KILLANN 13 0 147 0 0 22.2 13.1 UEXF0RH AA UX-005 KILLANN 0 0 <100 0 0 ERR ERR UEXFORD A UX-006 KILTEALY 20 0 •OOO 0 0 ERR ERF UEXFORH A UX-007 KILTEALY 20 0 174 0 0 18.1 10.6 UEXFORD A UX-008 KILTEALY 20 0 301 0 0 10.5 5. 6 WEXEORH AAA UX-009 KILTEALY 20 198 616 1 0 5.6 1.7 UEXFORD AAA UX-O1O KILTEALY 20 123 427 0 0 8.6 3.8 UEXFORD AAA UX-O11 ROSSARD 20 0 152 0 0 22.4 13.2 WEXFORD A UX-012 ROSSARD 20 0 189 0 0 23.2 13. 8 UEXFORD UX-013 ROSSARD 20 163 592 0 0 6.5 2.4 UEXFORD UX-014 ROSSARD 20 220 515 0 0 8.8 3.3 UEXFORD A UX-015 ROSSARD 20 0 <100 0 0 ERR ERR UEXFORP A UX-016 ST.MARYS 20 0 <100 0 0 ERR ERR WEXFORD AAA UX-017 ST.MARYS 20 0 262 0 0 9.4 5.3 UEXFORD AAA UX-018 ST.MARYS 20 0 <100 0 0 ERR ERI) UEXEORD AAA UX-019 ST.MARYS 20 0 <100 0 0 ERR ERR UEXFORD AAA WX-020 ST.MARYS 20 0 383 0 0 6.4 3.2 CARLOU A CU-OO1 COONOGUE 20 0 260 0 0 1.2.6 7.3 CARLOU AAA CU-002 COONOGUE IB 0 321 0 0 10.1 5.6 CARLOU A CU-003 COONOGUE 12 0 106 0 0 32.5 19.4 CARLOU A CU-004 COONOGUE 12 0 <100 0 0 ERR ERR CARLOU CU-005 COONOGUE 12 0 <100 0 0 ERR ERR CARLOU A CU-006 RATHANNA 20 0 389 0 0 9.2 5.0 CARLOU AAA CW-007 RATHANNA 20 0 389 0 0 9.2 5.0 CARLOU A CU-008 RATHANNA 20 0 <100 0 0 ERR ERR CARLOU A CU-009 RATHANNA 20 0 <100 0 0 ERR ERR CARLOU AAA CU-O1O RATHANNA 20 0 <100 0 0 ERR ERR CARLOU A CU-011 CRANEMORE 25 0 <100 0 0 ERR ERR CARLOU A CU-O12 CRANEMORE 25 0 389 0 0 9.2 5. 1 CARLOU A CW-013 CRANEMORE 25 0 <100 0 0 ERR ERR RANGE ANIHALS OVER COUNTY FLAG FARM NO.'S D.E.D. NO. OF SHEEP MIN MAX 600 Bq/K3 1000 Bq/f<3 K-1000 K-60 CARLOU A CU-O14 CRANEMORE 25 0 158 0 0 31.0 18.5 CARLOU A CU-015 MYSHALL 20 0 <100 0 0 ERR ERR CARLOU A CU-016 MYSHALL 20 0 <100 0 0 ERR ERR CARLOU A CW-O17 MYSHALL 20 0 <100 0 0 ERR ERR CARLOU AAA CU-018 MYSHALL 22 0 409 0 0 6.4 3.2 LAO1S A LS-OO1 ROSEN'S/CAPARD 38 0 123 0 0 26.1 15.4 LAOIS A LS-OO2 ROSEN'S/CAPARD 40 0 134 0 0 27.0 15.8 LAOIS A LS-003 ROSEN'S/CAPARD 22 0 <100 0 0 ERR ERH LAOIS A LS-004 CLONASLEE 24 0 <100 0 0 ERR ERR LAOIS A LS-005 CLONASLEE 25 0 <100 0 0 ERR ERR LAOIS A LS-006 CLONASLEE 25 0 136 0 0 18.4 10.7 LAOIS A LS-O07 CLONASLEE 25 0 <1CO 0 0 ERR ERR LAOIS A LS-008 BALLICK/NEUTOWN 27 0 <100 0 0 ERR ERR LAOIS A LS-O09 BALLICK/NEUTOUN 23 0 a oo 0 0 ERR ERR LAOIS A LS-010 BALLICK/NEUTOUN 25 0 <100 0 0 ERR ERR LAOIS A LS-O11 BALLICK/NEUTOUN 25 0 <100 0 0 ERR ERR LAOIS A LS-012 RATHSPIC/BALLYH 24 0 <100 0 0 ERR ERR LAOIS A LS-013 RATH5PIC/BALI.YH 25 0 145 0 0 19.5 11.4 LAOIS A LS-O14 RATHSPIC/BALLYH 25 0 <100 0 0 ERR ERR LAOIS A LS-015 RATHSPIC/BALLYH 26 0 <100 0 0 ERR ERR LAOIS A LS-O16 CARHTOWN 25 0 <100 0 0 ERR ERR LAOIS A LS-017 CARBTOWN 25 0 <10C 0 0 ERR ERR LAOIS A LS-018 CARDTOUN 25 0 112 0 0 24.6 14.8 LAOIS A LS-019 CARDTOWN 25 0 194 0 0 14.4 8.4 LAOIS A LS-020 MARY'NT/NEALS'N 35 0 162 0 0 20.1 11.5 LAOIS A LS-021 MARY'NT/NEALS'N 30 0 218 0 0 14.9 8.G LAOIS A LS-022 MARY'NT/NEALS'N 34 0 <100 0 0 ERR ERR OFFALY A OY-OOl TULLA 34 0 140 0 0 34.9 20.7 OEFALY A OY-002 TULLA 32 0 <100 0 0 ERR ERR OFFALY A OY-003 TULLA 33 0 203 0 0 16.9 9.G OFFALY A OY-004 KINNITY 25 0 177 0 0 20.0 11.0 OFFALY A OY-005 KINNITY 25 0 <100 0 0 ERR ERR OFFALY A OY-006 LETTER 30 0 104 0 0 39.8 23.6 OFFALY A OY-007 LETTER 40 35 205 0 0 18.5 10.0 OFFALY A OY-008 LETTER 30 0 346 0 0 11.0 6.4 OFFALY A OY-009 CLONMACNOISE 30 0 <100 0 0 ERR ERR OFFALY A OY-OIO CLUNMACNOISE 35 0 •noo 0 0 ERR ERR OFFALY A OY-O11 CLONMACNOISE 35 52 614 1 0 5.0 2.0 OFFALY A OY-012 HINDS 20 0 <100 0 0 ERR ERR OFFALY A OY-013 HINCS 22 0 359 0 0 8.1 4.2 OFFALY A OY-O14 HINDS 25 0 246 0 0 12.8 7.3 Nut ANIMALS OVER COUNTY FLAG FARM NO.'S D.E.D. NO. OF SHEEP MIN MAX 600 Bq/Kg 1000 Bq/K3 K-1000 K-600 OFFALY * OY-015 HINDS 20 0 112 0 0 27.5 16.2 OFFALY A OY-O1& HINDS 12 0 <100 0 0 ERR ERR OFFALY A OY-017 SHANNONBRIDGE 44 0 277 0 0 17.1 9.7 OFFALY A OY-018 SHANNONBRIDGE 24 0 <100 0 0 ERR ERR Ol-FALY A OY-019 SHANNONBRIDGE 32 0 180 0 0 17.7 10.2 OFFALY A OY-020 LEA 40 0 104 0 0 33.3 19. 2 OFFALY A OY-021 LEA 39 0 •aoo 0 0 ERR ERR OFFALY A OY-022 LEA 20 0 <100 0 0 283.9 170.2 OFFALY A OY-023 DERRYAIi 30 0 293 0 0 14.6 8.4 OFFALY A OY-024 DERRYAD 31 0 126 0 0 33.1 19.1 OFFALY A OY-025 DERRYAD 39 0 <100 0 0 ERR ERR OFFALY A OY-027 ROSCOMROE 20 0 124 0 0 23.3 13.6 OFFALY A OY-028 ROSCOMROE 20 0 142 0 0 20.9 12.2 OFFALY A OY-029 ROSCOHROE 20 0 <100 0 0 ERR ERR OFFALY A OY-O3O ROSCOMROE 20 0 <100 0 0 ERR ERR OFFALY A OY-031 ROSCOMROE 20 0 115 0 0 25.8 15.2 OFFALY A OY-032 RATHANGAN NO.2 25 0 146 0 0 26.7 15.8 OFFALY A OY-033 RATHANGAN NO.2 25 0 <100 0 0 ERR ERR OFFALY A OY-O34 RATHANGAN NO.2 25 0 <100 0 0 ERR ERR OFEALY A OY-035 RATHANGAN NO.2 25 0 <100 0 0 ERR ERR OFFALY A OY-036 GORTEEN 40 0 <100 0 0 ERR ERR OFFALY A OY-037 GORTEEN 23 0 <100 0 0 ERR ERR OFFALY A OY-038 GORTEEN 38 0 <100 0 0 ERR ERR OFFALY A OY-039 CLONBULLOGE 35 0 142 0 0 26.6 15.5 OFFALY A OY-040 CLONBULLOGUE 35 0 <100 0 0 ERR ERR OFFALY A OY-041 CLONBULLOGUE 22 0 <100 0 0 ERR ERR OFFALY A OY-042 CLONBULLOGUE 8 0 <100 0 0 ERR ERR OFFALY A OY-043 BALLYSHEAR 20 0 187 0 0 15.1 8. 6 OFFALY A OY-044 RAHEENKEERAN 20 0 •a oo 0 0 ERR ERR OFFALY A OY-045 CLONMACNOISE 20 0 567 0 0 4.3 1 .9 OFFALY A OY-046 CLONMACNOISE 20 47 185 0 0 22.0 12.3 LOUTH LH-OO1 RAVENSDALE 20 584 1208 18 9 0.5 -1.7 LOUTH LH-002 RAVENS1DALE 20 571 1304 19 6 0.6 -1.2 LOUTH AAA LH-003 RAVENSDALE 20 365 916 6 0 2.9 0.3 LOUTH LH-004 RAVENSDALE 19 233 657 2 0 4.8 1 .7 LOUTH LH-005 RAVENSDALE 20 218 674 2 0 4.7 1 .5 LOUTH LH-006 PRUMULLAGH 20 233 1447 17 8 0.2 -1 .1 LOUTH LH-007 HRUMULLAGH 20 0 979 5 0 2.4 0.8 LOUTH LH-008 HRUMULLAGH 20 200 943 6 0 2.6 0.5 LOUTH LH-009 DRUMULLAGH 21 153 869 8 0 2.8 0.4 LOUTH LH-O1O HRUMULLAGH 20 0 1077 2 1 2.7 1 .3 LOUTH + + LH-O11 RATHCOR 20 0 158 0 0 17.6 10.0 LOUTH l.M-012 RATHCOR 20 0 231 0 0 18.5 9.9 LOUTH LH-013 RATHCOR 20 116 338 0 0 12.6 6.3 KA NGE ANIMALS OVER COUNTY FLAG FARM NO.'S D. E . D. NO. OF SHEEP MIN MAX 600 Bq/Kg 1000 B q / K 3 K-1000 K-GOQ LOUTH LH-014 RATHCOR 20 202 664 1 0 S.O 1 .9 LOUTH LH-015 RATHCOR 20 170 506 0 0 7.5 2. 8 LOUTH LH-016 CARLINGFORD 20 0 1497 1 1 2.4 1 . 1 LOUTH LH-017 CARLINGFORD 20 0 103 0 0 32.4 19. 2 LOUTH LH-018 CARLINGFORII 20 0 124 0 0 26.2 15.0 LOUTH LH-019 CARLINGFORti 21 267 951 5 0 2.2 0.5 LOUTH + + LH-020 3ENKINSTOUN 20 0 204 0 0 13.7 8.0 LOUTH LH-021 3ENKINSTOUN 20 0 271 0 0 11.0 6.3 LOUTH LH-022 JENKINSTOUN 20 0 613 2 0 3.7 1 .4 LOUTH LH-O23 aENKINSTOUN 20 202 578 0 0 5.7 2 . 0 LOUTH LH-024 JENKINSTOUN 20 0 527 0 0 5.2 APPENDIX 2 RESULTS OF ON-FARM MEASUREMENTS (COMPILED BY DED) 53 RANGE ANIMALS OVER COUNTY FARM NO's DED NO OF SHEEP MIN MAX 600 liq/Kg 1000 Bq/Kg DONEGAL DL-001 TO 006 MEENCARGAGH 140 0 2213 97 66 DONEGAL DL-007 TO 010 KILLYMASNY 100 0 905 6 0 DONEGAL DL-011 CROWKEERAGH 25 271 64 7 1 0 DONEGAL DL-012 TO 016 SEACOR 125 0 1461 39 10 DONEGAL DL-017 TO 020 GARTAN 94 0 979 24 0 DONEGAL DL-021 TO 024 CHURCHILL 100 0 1349 25 3 DONEGAL DL-025 TO 029 DUNLEWY 125 215 1697 60 3 DONEGAL DL-030 TO 033 CROVEHY 100 250 1289 54 12 DONEGAL DL-034 TO 038 MAGHERACLOGHER 125 0 959 26 0 DONEGAL DL-039 TO 043 ARRANMORE 125 0 275 0 0 DONEGAL DL-044 TO 047 GLENLEHEEN 93 207 1357 68 12 DONEGAL DL-04S TO 050 FINTOWN 70 0 957 33 0 DONEGAL DL-051 TO 056 ALTNAPASTE 144 0 1775 119 43 DONEGAL DL-057 TO 061 CLOGHAN 125 0 2077 75 41 DONEGAL DL-062 TO 0f>7 GLENTOGHER 150 0 698 13 0 DONEGAL DL-068 TO 072 GRAFFY 125 328 1552 104 48 DONEGAL DL-073 TO 077 TAWNAWULLY 125 0 1151 27 2 DONEGAL DL-078 TO 082 LOUGH EASK 107 103 735 10 0 DONEGAL DL-083 TO 005 TEMPLECARN 75 0 1463 17 3 DONEGAL DL-0P6 TO 090 GROUSEHALL 125 0 961 33 0 DONEGAL DL-091 TO 095 LETTERMORE 125 0 1859 87 50 DONEGAL DL-096 TO 099 TERMON 100 0 1231 61 7 DONEGAL DL-100 TO 103 GLEN 100 0 1271 15 3 DONEGAL DL-10-1 TO 106 PETT1GO 75 259 1485 67 24 DONEGAL DL-107 TO 111 EANYMORE 125 0 1483 93 16 s DONEGAL DL-112 TO 115 LAGIIY 100 0 1213 59 6 DONEGAL DL-116 TO 119 GOLAND 100 0 1145 31 3 DONEGAL DL-3 20 TO 124 CREEN/"WEAR 120 115 2005 77 38 DONEGAL DL-125 TO 130 DOOI.iH 145 0 1854 94 47 DONEGAL DL-131 TO 135 CLOGHER 125 0 1627 81 38 DONEGAL DL-136 TO 140 TULLYNAUCHT 122 0 1697 53 18 DONEGAL DL-141 TO 143 DOOCHARY 75 279 1069 38 2 DONEGAL DL-144- TO 146 CLOCHAN 75 342 1762 68 43 DONEGAL DL-147 GRAFFY 25 459 1305 23 13 SLIGO SO-001 TO 005 BRANCHFIELD 80 0 133 0 0 SLIGO SO-006 TO 009 SKREEN 100 0 1015 10 1 SLIGO SO-010 TO 014 TEMPLEBOY STH. 100 0 1668 54 16 SLIGO SL-015 TO 019 BUNCROWEY 97 0 713 6 0 SLIGO SL-020 TO 021 ACLARE 37 0 624 1 0 SLIGO SL-022 TO 026 KILMACTEIGE 99 0 860 4 0 SLIGO SO-027 TO 031 BREENCORRAGH 100 137 1453 23 2 SLIGO SO-032 TO 036 GLENDARRAGH 100 106 1559 40 16 SLIGO SO-037 TO 041 MULLAGIIEPUSE 100 125 776 18 0 SLIGO 50-042 TO 046 CLOONACOOL 100 0 680 1 0 SLIGO SO-047 TO 051 TEMPLEVANY 97 0 74 7 1 0 SLIGO SO-052 TO 055 LOUGHIL 80 0 1275 20 10 SLIGO SO-056 TO 060 SHANCOUfiH 101 0 2229 21 19 SLIGO SO-061 TO 065 BAIXYNASHEE 94 0 930 18 0 KAN Ol-J ANIMALS OVER COUNTY FARM NO' s DED NO OF SHEEP MIN MAX 600 Eq/Kg 1000 hcj/Kg LEITRIM LM-001 TO 005 DRUMAHAIRE 100 0 1521 19 8 LEITRIM LM-906 TO 007 KILLANUMERY 40 0 183 0 0 LEITRIM LM-OOB TO 012 ARIGNA 100 0 1100 G LEITRIM LM-013 TO 017 KILE.ARGA 100 0 752 6 0 LEITRIM LM-01U TO 022 MAHANAG11 95 0 740 4 0 LEITIilM LM-023 TO 024 ST.PATRICKS 39 0 1138 11 1 LEITRIM LM-025 TO 029 GLENDO'/ 100 0 793 10 0 LEITRIM LM-030 TO 034 CLOONCLARE 103 0 2152 54 LEITRIH LM-035 TO 039 M1HAMILTON 100 0 1263 29 4 LEITRIM LM-040 TO 044 GLENFARN 100 0 549 0 0 LEITPIM LM-04 5 TO 049 LURGANBOY 100 0 1022 Hi 2 LEITRIM LM-050 TO 054 GLENADE 101 0 1306 17 4 LEITRIM LM-055 TO 059 AGHALATEEVE 98 0 612 0 LEITRIM LM-060 TO 064 AGHAVOCHIL 100 0 231 0 0 LEITRIM LM-065 TO 069 GLENANIFF 97 0 14 00 47 6 LEITRiy, LM-070 TO 074 YUGAN 91 0 1434 34 11 LEITRIM LM-0 75 TO 079 DRUMREILLY E. 100 0 1395 49 11 LEITRIM LM-030 TO 004 DRUMRE1LLY W. 100 0 1574 20 4 LEITRIM LM-085 TO 090 BARNAMEENAGH 100 0 1323 18 4 LEITRIM LM-091 TO 094 STRAI.ONCFORD 100 0 1263 40 B CAVAN CN-001 TO 004 TIRCAHAN 81 0 694 5 r 0 CAVAI: CN-00 , TO 009 BAWNnOY 95 0 283 0 0 CAVAH CM - 010 TO 014 CHANLINEAR 98 0 1175 20 3 CAVA'.' CN-oir.. TO 019 KINAKLF.Y 100 0 1391 36 7 CAVA:I CN-020 TO 024 PEDRAVOHERS 101 0 1023 29 1 CAVA:; CH-025 TO 029 BENBRACK 104 0 1776 45 IB CAVAN CN-030 TO 034 DERRYNANTA 100 0 1442 2 5 12 CAVA:: CN-035 TO 039 DUNMAKEEVER 100 0 854 6 0 CAVA.M CN-04 0 TO 04 4 TOWRA 100 0 1247 35 5 CAVAi.' CN-045 TO 049 DERRYLAHAN 104 0 1324 22 4 CAVAH CN-050 TO 054 TUAM 104 0 1071 39 2 CAVA.V CN-055 TO 050 TEEBANE 85 0 1135 49 & CAVA!-; CN-059 TO 063 KILLINAGH 103 0 780 14 0 CAVA!.' CN -004 TO 00 0 EJ'KKY 97 0 371 0 0 ROGCOM;-:O:1 RK-OO] TO 005 KEADUE 84 0 559 0 ROSCOMMOI) RH-OO& TO 010 ALTAGOWLAN 88 0 1513 14 ROSCW'.KOI RH-011 TO 014 LOUGH ALLEN 00 0 1333 24 ROSCOMKO! ' RN-015 TO 021 BALLYFARNAN 112 0 678 2 ROSCOMXlT' RH-0 22 TO 026 AGHAFIN 70 0 511 0 ROSCOMKOr RN-07.7 TO 031 CROSf.NA 70 0 <100 0 R0SC0!W>! RN-012 TO 035 B0Y1.F. 30 0 UOO 0 RO.SCOKMO: RN-03T, TO 041 T1VAMACH 90 0 104 0 ROSCOI^O: Rl-J- 0 •",'.'. nALLYFi:!-:KOYL 20 0 171 0 ROSCOMMI RfJ- 0.13 CREAM 15 0 4 32 0 HAN ANIMALS OVER COUNTY FARM NO ' s DED NO OF SHEEP MIN MAX 600 Bq/Kg 1000 Bq/Kg MAYO MO-001 TO 005 KILGARVAN 125 0 794 3 0 MAYO MO-006 TO 010 5ALLYM0UNT 125 0 880 8 0 MAYO MO-011 TO 014 ATTYMASS E. 100 0 1140 20 4 MAYO MO-015 TO 019 BUNAVEELA 125 0 598 0 0 MAYO MO-020 TO 024 GLENCO 125 0 535 0 0 MAYO MO-025 TO 028 SHESKIN 100 0 645 3 0 MAYO MO-029 TO 033 KNOCKNALOWER 125 0 704 1 0 MAYO MO-034 TO 030 DERRY 125 0 818 2 0 MAYO MO-039 TO 042 BALLYCASTLE 73 0 605 1 0 MAYO MO-043 TO 04 6 MUINGS 100 0 297 0 0 MAYO MO-047 TO 048 ATTYMASS W. 50 0 290 0 0 MAYO MO-0'19 TO 052 BALLYOVEY 100 0 357 0 0 MAYO MO-053 TO 057 SRAHMORE 125 0 693 1 0 GALWAY G-001 TO 005 LErrERBRICKAUN 123 0 349 0 0 GALWAY G-006 TO 010 KILLANNIN 121 0 788 9 0 GALWAY G-Oll TO 015 ILLION 125 0 670 1 0 GALKAY G-016 TO 020 CAMUS nr> 0 760 4 0 GALWAY G-021 TO 025 KNOCKDOY 125 0 575 0 0 GALWAY G-02& TO 027 LOUGHATORICK 42 0 460 0 0 GALWAY G-028 TO 030 COOS 69 0 550 0 0 GALWAY G-031 TO 037 DRUMMIN 168 0 525 0 0 O5 CLARE CE-001 TO 003 DRUMMAAN 75 0 166 0 0 CLARE CE-004 TO 008 INISHCALTRA 112 0 216 0 0 CLARE CE-009 TO 013 MOUNTSHANNON 115 0 445 0 0 CLARE CE-014 TO 018 CLOONUSKER 105 0 867 1 0 CLARE CE-019 TO 023 CAPPAGHABAUN 117 0 179 0 0 CLARE CE-024 TO 028 KILLANENA 125 0 <100 0 0 KERRY KY-001 TO 005 BOOLTEENS 104 0 393 0 0 KERRY KY-006 TO 010 KILGARYLANDER 107 0 497 0 0 KERRY KY-011 TO 015 LACK 114 0 536 0 0 KERRY KY-016 TO 020 INCH 111 0 395 0 0 KERRY KY-021 TO 025 BALLINVOHER 111 0 495 0 0 KERRY KY-026 TO 030 BALLINACOURTY 116 0 426 0 0 KERRY KY-031 TO 035 MINARD 114 0 292 0 0 KERRY KY-036 TO 040 KINARD 112 0 324 0 0 KERRY KY-041 TO 04 5 GLIN 98 0 219 0 0 KERRY KY-046 TO 049 GLANLEE 98 0 495 0 0 KERRY KY-050 TO 054 GLANLOUGH 125 0 783 6 0 KERRY KY-055 TO 059 KILGAP.VAN 123 0 764 2 0 KERRY KY-060 TO 064 CAPPAGH 125 0 521 0 0 KERRY KY-065 TO 069 BANAWN 120 0 64 7 1 0 KERRY KY-070 TO 074 GLANMORE 116 0 577 0 0 KERRY KY-075 TO 080 ARDEA 106 0 358 0 0 KERRY KY-000 TO 004 DAWROS 121 0 538 0 0 KERRY KY-08li TO 088 KENMARE 95 0 369 0 0 RANGE ANIMALS OVER COUNTY FARM NO'5 DED NO OF SHEEP MIN MAX 600 Bq/Kg 1000 Bq/K COM:: C--0LU oor. KILNAMA"AGH 100 302 CORK c-ooc- 0 1 0 COULAUli 112 300 CORK K1LLACONF.NAGH 10 3 361 C-0I1 015 B5 350 CCi:K C - 01 0 C20 K ILCATH1 :R I KT. CORK 025 KILCASK1H 107 227 C-021 Kll.CA^K1.:-! 102 3 2 8 CORK c-u::i'.. o :< o CORK AIIIL B7 305 C-031 106 324 CORK C-03b 0-10 DOUCK CORK 04 5 KEALKTL 105 408 C-041 231 CORK C-04C USO MEALAC.ll 102 CORK 055 BANTRY 100 162 C-O'JI 283 CCP.K C-05b 060 BEAR 100 CORK 065 DURRUS WEST 100 372 C-Of.l 343 CORK C-Oof- 069 GLENLOUGH 00 CORK 072 SHKEPS HEAD 52 343 C-070 376 CORK C-07 3 077 DURRUS EAST 100 COHK 002 DUNDEACON 100 300 C-U70 337 COP." C- OP.? 0 86 DUNMANU2 00 CORK O'JO SC1UJLL 80 330 CORK c-onv 0'VJ CURRVGLASS 100 408 CORK C- O'Jl 100 GLENGARR1FF 106 350 CORK C-096 104 266 1 DAFXYBANE ao 300 CORK C-10 : 109 BALLYDEHOB loo CORK C-105 114 322 CROOKHAVEN 100 266 CORK c-no 119 GOLEEN 100 C- I1.'-. 00 WATEF-.rORlJ WD-001 TO 005 TINNISAGGART 105 1445 29 14 WATEREORD WD-Oul"-, TO 009 CAPPOQUIN 111 1316 58 11 KATERKORD WD-010 TO 013 KKOCK-BRANDAUM 96 1243 19 2 A'ATERFORD KD-014 TO 017 GRAIGNAGOMER 87 1032 14 1 WATERFORD KD-01B TO 023 ST-MARYS 99 979 38 0 WATERF0RD WD-024 TO 029 GURTEEN 98 1650 32 15 WATERFORD KD-030 TO 0 33 FEWS 35 477 0 0 WATERFORD WD-034 TO 039 COURMARAGLIN 54 766 3 0 KATERFORD WD-04 0 TO 04 5 BALLMACARDRY 99 2031 44 25 WATERFORD WD-04 6 TO 047 ROSS 30 1069 2 1 WATERFORD WD-040 TO 053 B.'XLYSAGGAFiT 107 2136 59 26 WATERFORD WD-055 TO 092 BALLYIN-H. 125 2996 99 88 WATERFORD WD-054 TO 085 BALLYIN-L. 15 <100 0 0 WATERFORD WD-058 TO 06,3 BALLY DUFF 35 <100 0 0 WATERFORD WD-065 TO 068 RATHG0RI-1ACK 38 823 3 0 WATERFORO WD-064 TO 07 5 COMERACH 125 1324 22 3 WATERFORD WD-079 A1CD 081 COURMARAGLIN 58 1463 24 10 WATEREORD WD-086 TO 090 SESKINAN 85 1256 22 TIPFERARY IT.-00] TO 005 NEWCASTLE. 100 0 1077 27 1 TIPPERARY TS-006 TO 010 CLOGHEEN 145 0 1701 28 12 TIPPERARV TS-012 TO 0 3 5 COOLG'ANROE 100 0 768 4 0 TIPPERARY TS-010 TO 020 BURNCOURT 113 0 850 2 0 7.'?-02] TUDBRID 10 0 34 5 0 0 KAN ANIMALS OVER COUNTY FARM NO's OED NO OF SHEEP MIN WAX COO Bq/Kg 1000 Dq/Kg TIPPKRARY TS-O22 TO 023 KILCOMMON 50 0 68?. 1 0 T1PPERARY TS-024 TO 02B TEMPLENEIRY 101 0 130T, 52 13 TIPPF.RARY TS-029 TO 033 CLONBEG 9B 165 1346 45 6 KEXFORD WX-001 TO 005 KILLANN 63 0 147 0 0 WEXFORD WX-006 TO 010 KILTEALY 100 0 616 1 0 WEXFORD WX-011 TO 015 ROSSARD 100 0 592 0 0 WEXFORD WX-016 TO 020 ST.MARYS 100 0 383 0 0 CARLOW CW-001 TO 00b COONOGUE 74 0 321 0 0 CARLOW CW-0Q6 TO 010 RATHANNA 100 0 389 0 0 CARLOW cw-on TO oil CRANEMORE 100 0 389 0 0 CARLOW cw-oir. TO ois MYSHAIX fl?. 0 409 0 0 LAOTS LS-OOl TO 003 ROSEN'S/CAPARD 100 0 134 0 0 LAO IS LS-004 TO 007 CLONASLEE 99 0 136 0 0 LAO IS LS-000 TO Oil BALLICK/NEWTOWN 100 0 06 0 0 LAO IS LS-0I2 TO 015 RATHSPIC/DALLYH 100 0 14 5 0 0 LAO IS LS-016 TO 019 CARDTOWN 100 0 194 0 0 LAO IS LS-020 TO 022 MARY'NT/NEALS'N 99 0 218 0 0 OFFALY OY-001 TO 003 TULLA 99 0 203 0 0 OFFALY OY-004 TO 005 KINNITY 50 0 177 0 0 OFFALY OY-006 TO 008 LETTER 100 0 346 0 0 OFFALY OY-009 TO Oil CLONMACMOISE 100 0 614 1 0 OFFALY OY-012 TO 016 HINDS 99 0 359 0 0 OFFALY OY-017 TO 019 SHANNONBRIDGE 100 0 277 0 0 OFFALY OY-020 TO 022 LEA 99 0 104 0 0 OFFALY OY-023 TO 026 DERRYAD 100 0 293 0 0 OFrALY OY-027 TO 031 ROSCOMROE 100 0 142 0 0 OFFALY OY-032 TO 035 RATHAKGAN NO.2 100 0 146 0 0 OFFALY OY-036 TO 038 GORTEEN 101 0 72 0 0 OFFALY OY-039 TO 042 CLONBULLOGE 100 0 142 0 0 OFFALY OY-043 BALLYSHEAR 20 0 1(37 0 0 OFFALY OY-044 RAHEENKEERAN 20 0 47 0 0 OFFALY OY-045 TO 046 CLOKMACNOISE 40 0 567 0 0 LOUTH LH-001 TO OOS RAVENSDALE 99 218 1304 47 15 LOUT!! LH-006 TO 010 DRUKULLAGH 101 0 1447 38 9 LOUTH LH-011 TO 015 RATHCOR 100 0 664 1 0 LO'.mi LH-010 TO 019 CARLINGFORD 81 0 1497 6 1 r.oin'h- I.H-020 TO 024 JENKINSTOWN 100 0 613 2 0 APPENDIX 3 COUNTY MAPS SHOWING MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED 61 CARLOWAND WEXFORD MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED N DEDS over 2000 Bq/Kg • DEDs over 1500 Bij/Kg M DEDS over 1000 Bq/Kg M DEDS over 600 Bq/Kg M DEDS under 600 Bq/Kg H DEDS not monitored • 62 CAVAN MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DSDs over 2000 Bq/Kg DSDs over 1500 Bq/Kg DSDs over 1000 Bq/Kg DSDs over 600 Bq/Kg DEDs under 600 Bq/Kg DSDs r.ot monitored CLARE MAXIMMUM ACTIVITY MEASURED IN EACH DED MONITORED DEDs over 2000 Bq/Kg DEDs over 1500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored CORK MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DEDs over 2000 Bq/Kg DED&- over- 1500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored 66 N GALWAY A MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DEDs over 2000 Bq/Kg DEDs over 1500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored KERRY MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DEDs over 2000 Bq/Kg DEDs over 1500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored L-WIS AND OFFALY MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DSDs over 2000 Bq/Kg D5DS over 1500 Bq/Kg D?Ds over 1000 Bq/Kg ever 600 Bq/Kg • zDs re' monitored I.EITRIM MAXIMUM ACTWIYMEASURED IN EACH DED MEASURED DEDs over 2000 Bq/Kg DEDs over 1Z00 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored 70 LOUTH MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED Dc'Ds over 2000 Bq/Kg DEDs over 1500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored 71 MAYO MAXIMUM ACTIVITY MEASURED IN ELACH DED MONITORED N DEDS over 2000 Bq/Kg DEDs over 1500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored ROSCOMMON MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DEDs over 2000 Bq/Kg DEDs over 1500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored SLICO MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DEDs over 2000 Bq/Xg DEDs over 2500 Bq/Xg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Xg DEDs under 600 Bq/Xg DEDs not monitored TIPPERARY DEDs over 2000 Bq/Kg MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DEDs over 2 500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored 75 WATERFORD MAXIMUM ACTIVITY MEASURED IN EACH DED MONITORED DEDs over 2000 Bq/Kg DEDs over 1500 Bq/Kg DEDs over 1000 Bq/Kg DEDs over 600 Bq/Kg DEDs under 600 Bq/Kg DEDs not monitored