Groundwater protection zones for community drinking water supply - - PowerPoint PPT Presentation

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Groundwater protection zones for community drinking water supply - - PowerPoint PPT Presentation

Groundwater protection zones for community drinking water supply wells in the Wellington Region Mike Toews 30 May 2018 GNS Science Who Am I? Mike Toews (pronounced Taves) Studied as a Hydrogeologist and Groundwater Modeller in Canada,


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Groundwater protection zones for community drinking water supply wells in the Wellington Region

Mike Toews 30 May 2018

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Who Am I?

  • Mike Toews (pronounced Taves)
  • Studied as a Hydrogeologist and Groundwater

Modeller in Canada, with a M.Sc. Degree

  • Over ten years of experience as a GW modeller
  • Employed by GNS Science since 2011
  • First capture zone work from 2006, as part of my

M.Sc. Degree

  • Developed CZs for several areas in Waikato
  • Developed CZs for Wellington in 2015
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Purpose

  • Present mapped groundwater protection zones

to drinking water supply wells

  • Discuss how the zones can be used to protect

against discharges to land from:

– Microorganisms (<1 year residence time) – Other potential contaminants that are more persistent or accumulate with distance and time

§ 1.1, p. 1

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Capture zone (CZ)

Total source area where water may potentially travel from Protection against non-easily degraded chemicals

Protection zone (PZ)

Protection against pathogens

(distance/ 1-year travel time)

Definitions

§ 1.2, p. 2–3

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Attached / detached PZ

  • Fig. 1.2, § 1.2, p. 3
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Scope of report

  • Use existing GW models

– Hutt Valley – Mark Gyopari’s HAM3 model – Kapiti Coast – Doug’s model – Wairarapa Valley – Mark & Doug’s FEFLOW models

  • Methods similar to Toews & Donath (2015)

– Similar resources and uncertainty simulations – Simplified language and mapped outputs

  • Use PNRP Schedule M2 wells
  • Evaluate a range of PZ time thresholds

– 1-year, 2-year, 5-year, etc.

§ 1.1, p. 1–2

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Methods

  • Groundwater flow models
  • Particle tracking

– Forwards and backwards – From groundwater table to well (saturated only)

  • Time-based methods

– Hard science for pathogen removal based on decay rates over distance (i.e. distance-based) – PZs defined by travel time from water table to well – Conservative to include extra distance

  • Sensitivity analysis

– Multiple models used, different flow paths – Parameters were adjusted ±25% – Simplest way to consider preferential flow pathways

§ 3, p. 7–9

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Areas

  • Fig. 1.1, § 1.1, p. 1
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Hutt Valley

  • Model runs for 5 years, between 2007–2012
  • Extends beneath Wellington Harbour
  • Simulates interaction between Hutt River, Ocean

and the Wai

Location WRC Well number Description

Petone R27/7354 Buick Street public bore Gear Island BQ32/0033 Gear 3 Gear Island BQ32/0034 Gear 2 Gear Island BQ32/0035 Gear 1 Waterloo R27/4064 Colin Grove Waterloo R27/0001 Hautana Street Waterloo R27/4063 Bloomfield Terrace Waterloo R27/1179 Penrose 7 Waterloo R27/4057 Penrose 4 Waterloo R27/1180 Willoughby 8 Waterloo R27/4058 Willoughby 5 Waterloo R27/1181 Mahoe 6

Table 2.3 § 2.2, p. 5

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Hutt Valley

  • Fig. 4.1, p. 11

§ 4.2, p. 10–11

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Hutt Valley

  • Provisional PZ

based on geology (Begg & Morgenstern, 2017)

  • SW extent where

Petone Marine Beds change between thin to continuous aquitard

  • Boundary can be

refined (Begg)

S42A Loe (2018)

  • p. 55–57
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Kāpiti Coast

  • Longest running model, 19 years (1992–2011)
  • Simulates several aquifers, 38 km long

Location WRC Well number Description

Ōtaki R25/5228 Rangiuru Road Bore Ōtaki R25/5235 Tasman Road Bore Hautere S25/5379 next to Ōtaki River Hautere S25/5443 next to Ōtaki River Waikanae R26/6291 K4 – Cooper 1 Waikanae R26/6293 K5 – Ngā Manu Waikanae R26/6299 K12 Waikanae R26/6307 Kb4 – Landfill Waikanae R26/6311 KB7 Waikanae R26/6559 Otaihanga Bore PW1 Waikanae R26/6664 Otaihanga Bore PW5 Waikanae R26/6666 Rangihiroa – not implemented Waikanae R26/6804 K10 – Market Garden Waikanae R26/6839 K6 – Wooden Bridge Waikanae R26/7255 N2 Paekakariki R26/7158 adjacent to water treatment plant

Table 2.4, p. 6 § 2.3, p. 5–6

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Ōtaki

  • Fig. 4.2

§ 4.3, p. 12

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Hautere

  • Fig. 4.3, p. 13

§ 4.3, p. 12–13

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Waikanae

  • Fig. 4.4, p. 14

§ 4.3, p. 13–14

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Paekakariki

  • Fig. 4.5, p. 15

§ 4.3, p. 14–15

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Wairarapa Valley

  • Three separate FEFLOW models
  • 15 to 16 years (1992 to 2007/2008)

Model Location WRC Well number

UV Opaki T26/0259 UV Masterton T26/0243 UV Masterton T26/0549 UV Wainuioru T26/0492 UV Wainuioru T26/0493 MV Carterton S26/0705 MV Carterton S26/0824 MV Carterton S26/0919 MV Greytown S26/0880 MV Greytown and Featherston BP33/0008 MV Greytown and Featherston BP33/0009 MV Greytown and Featherston BP33/0022 LV Martinborough S27/0396 LV Martinborough S27/0404 LV Martinborough S27/0695 LV Martinborough S27/0910

Table 2.5 § 2.4, p. 6

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Masterton

  • Fig. 4.6

§ 4.4, p. 16

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Carterton

  • Fig. 4.7, p. 17

§ 4.4, p. 16–17

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Greytown and Featherston

  • Fig. 4.8, p. 18

§ 4.4, p. 17–18

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Martinborough

  • Fig. 4.9, p. 19

§ 4.4, p. 18–19

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Discussion

  • Different sizes and shapes of PZs
  • Overconservative, but targeted to cover land

where groundwater may flow to a well

  • Groundwater sourced from:

– Rainfall recharge from land surface – Surface water recharge from streams, rivers

  • Drinking water standard requires groundwater to

have at least 1-year residence time

  • National Environmental Standard (NES) is

legislation to preserve drinking water quality

§ 5, p. 20–21

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Recommendations

  • 1-year PZs can be used to protect against

microorganisms

  • Older PZs can be used to protect against other

contaminants with longer filtration or decay times

  • Detached PZ may require an additional arbitrary

fixed radius zone around wellhead (min. 5 m)

  • PZs should be re-evaluated with new models,

information, wells, pumping scenarios, etc.

§ 6, p. 23

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Questions

Mike Toews m.toews@gns.cri.nz