New Zealand Journal of Marine and Freshwater Research abstracts
1998/99 national survey of pesticides in groundwater using GCMS and ELISA
MURRAY E. CLOSE
Institute of Environmental Science
& Research Ltd
P. O. Box 29 181
Christchurch, New Zealand
email: murray.close@esr.cri.nz
MICHAEL R. ROSEN
Wairakei Research Centre
Institute of Geological & Nuclear Sciences Ltd
Private Bag 2000
Taupo, New Zealand
email: m.rosen@gns.cri.nz
Abstract A total of 95 wells throughout New Zealand were
sampled during summer 1998/99 and analysed for a range of pesticides using gas
chromatography-mass spectroscopy (GCMS). Thirty-three wells (35%) had
pesticides including triazine metabolites detected, with 18 wells (19%) having
two or more pesticides detected. Only one well (K38/0172) had pesticides
detected at levels greater than the maximum acceptable value (MAV) for drinking
water. There were 20 different pesticides detected, usually at very low
concentrations, as well as two triazine metabolites. Fifty-seven out of the 75
pesticide detections (76%) belonged to the triazine group, with only five of
these (9%) being >1 mg m
-3 and 74% of these being <0.1 mg
m
-3. Three of the 18 non-triazine pesticide detections (17%) were
>1 mg m
-3 with all three detections being in Well K38/0172. About
half (44%) of the non-triazine pesticides were <0.1 mg m
-3. Apart
from Well K38/0172, the highest levels of pesticides with respect to the MAV
were seen for simazine and terbuthylazine, which were 16 and 44% of the MAV,
respectively, with the remaining pesticides all below 4% of their MAV. This
indicates that, although there were very low levels of pesticides present in
35% of the wells, there would be no significant health risk based on the
pesticides analysed from drinking the groundwater investigated with the
exception of Well K38/0172. There was a significant decrease in the detection
limits for many pesticides for the 1998/99 survey compared to the two earlier
surveys. When the detection limits for the earlier surveys were applied to the
present survey there would have been a total of 10 wells out of the 95 sampled
(11%) with pesticides detected. This compared with 7% of the 82 wells in 1990
and 13.6% of the 116 wells in 1994 with detectable pesticides, indicating that
a similar percentage of wells have had detectable pesticides in each survey
once correction for variable detection limits has been made. There was a
significant difference between wells with and without pesticide detections for
the following factors: wells with pesticide detections had shallower well
screens, were screened nearer the water table, had lower pH values and higher
nitrate levels. Samples for analysis using two enzyme-linked immunosorbent
assay (ELISA) atrazine test kits were collected at the same time as the other
pesticide samples. The "normal" atrazine ELISA test kit only showed four
positive detections, mainly because of a relatively high detection limit. The
high sensitivity (HS) atrazine test kits detected pesticides in 20 of the 28
samples that were tested. Nineteen of the 20 detections had pesticide
detections using GCMS, with the other eight samples having no pesticides
detected using GCMS. The HS atrazine ELISA test kit appears to be a useful
indicator of pesticide contamination for New Zealand groundwater systems at a
relatively low level of detection. All the positive GCMS results that were
tested gave positive test kit results and there was only one potential false
positive result. This is probably because the majority of pesticides detected
in groundwater in New Zealand are triazines, and the HS atrazine kit has cross
reactivity with most triazines and related pesticides.
Keywords pesticide; groundwater; ELISA; New Zealand
M00044
Received 3 July 2000; accepted 25 October 2000
New Zealand Journal of Marine and Freshwater Research, 2001, Vol. 35:
205-219
0028-8330/01/3502-0205 $7.00 (c) The Royal Society of New Zealand
2001
PDF file of entire paper: medium quality (1125K); (scanned from paper original: notes about this process)
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