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The role of commercial plantation forestry in the status of our water quality What does the data tell us Water clarity by dominant land cover 2009-13 Metres (Max value: 12.3m) ANZECC 2000 guideline Urban Indigenous Exotic forest


  1. The role of commercial plantation forestry in the status of our water quality

  2. What does the data tell us Water clarity by dominant land cover 2009-13 Metres (Max value: 12.3m) ANZECC 2000 guideline Urban � Indigenous � Exotic forest Pastoral � Dominant land cover � Source: NIWA; regional councils

  3. What does the data tell us Dissolved phosphorus by dominant land cover 2009-13 mg/m 3 100 (Max value: (Max value: 90 270 mg/m 3 ) 290 mg/m 3 ) 80 70 60 50 40 Dissolved phosphorus 30 threshold 20 10 0 Urban � Indigenous � Pastoral � Exotic forest Dominant land cover Source: NIWA: regional councils

  4. What does the data tell us Nitrate-nitrogen by dominant land cover 2009-13 mg/ m 3 2,500 NPS-FM nitrate- nitrogen guideline B 2,250 (Max value: 2,000 13 1 500 mgim 3 ) 1,750 1,500 1,250 1,000 750 500 250 I ndigenous � � Urban zyxwvutsrqponmlkjihgfedcbaZYXWVUTSRQPONMLKJIHGFEDCBA Pastoral � Exotic forest Dominant land cover Source: NI WA; regional councils

  5. What does the data tell us E.coli concentration by dominant land cover 2009-13 E.coli per 100mL 1,100 NPS-FM guideline 1,000 (Max value; (Max value: 900 1,750 E.co/i/100mL) 2,300 E.coii/100mL) 800 700 600 500 400 300 200 100 0 Urban � Indigenous � Exotic forest Pastoral � Dominant land cover Source: NIWA; regional councils

  6. National Data = generally encouraging Other regions � Auckland 6% of sam ple Land cover Water Quality Water Quality • National datasets Index Class Native 91.7 Excellent generally indicates Exotic Forest 81.9 Good plantation forests WNW Rural 66.7 Fair Urban 54,3 Fair maintain an average status a bit below undisturbed native forest but above pastoral 5 farming and urban. • Other regional data confirms.... Nathe Exotic Forest � Rural Urban But pure forest sites underrepresented. Land Cover PFOLSEN

  7. 2001-02 zyxwvutsrqponmlkjihgfedcbaZYXWVUTSRQPONMLKJIHGFEDCBA � 120 2002-03 � 131.1111 2003-04 � 100 Other examples 2004-05 � 136.3636 2005-06 135.4545 2007-08 � 141.1111 2008-09 � 131.25 2012-13 � 123.8095 Mangapapa Bay of Plenty West Coast 2013 MCI results German Moores Palmers Gully Sunday Austrians Redjacks Ongionui Blackmum Location Creek Ck Creek (12 Mile) s Ck Creek Creek Stream MCI 146 139 130 114 116 145 136 127 QMCI 6 6 8 8 6 7 8 8 Sunday Creek Estimated fishing area = 220m2 Fish abundance (fish/m2) 2003 2006 2008 2010 MCI 160 Longfin eel 0.073 0.095 0.005 0 Shortfin eel 0 0.009 0.005 0 140 0 Inanga 0 0 0 120 0.06 0.01 0 Koaro 0.16 Shortjaw kokopu 0 0 0 0 100 Banded Kokopu 0.28 0.36 0.11 0.02 80 Brown trout 0 0 o o Bluegill bully 0 0 0 0 60 Upland bully 0 0 0 0 40 0.04 0.03 0.05 0 Redfin bully Dwarf galaxias 0 0 0 0 20 Lamprey 0 0.015 0 0 0

  8. Water Temperature Measured from a long term in-forest monitoring site during harvest. Native fish have m axim um tem perature acceptability of approxim ately 2 5 ° C ( shortfin and longfin eels) and about 2 0 ° C for m any bully species and below 2 0 ° C for trout and galaxid species. I ntroduced sport fish ( salm on and trout) are stressed w hen tem peratures exceed 2 0 ° C ( Quinn, Hickey, 1 9 9 0 ) . W hen considering m acroinvertebrates w ater tem perature is a key determ inant of diversity. Stoneflies are largely confined to rivers betw een 1 3 and 1 9 ° C and m ayflies are less com m on in rivers w ith m axim um tem peratures greater than 2 1 .5 ° C ( Quinn, Hickey, 1 9 9 0 ) . per. Moo. Av 3 . ( 1 . Toreturba exits Exotic Forest) • Exotic Forost/Farrniona) - 5 Per. Mee. Avg. ( 2 . Ye Paid - bridge 5 per. Moo. Av 3 . ( 3 .Zittel Jm n Exotic/ Native Forest> - per. Moo. Avg. ( 4 . Farm land- Ent., nog bras° 5 pen Mov. As 3 . ( S. Trubutery Ex forst a Pierce Rd) - 5 per. Mov. Avg. ( 6 . Ye Peel exiting forest) - 5 zyxwvutsrqponmlkjihgfedcbaZYXWVUTSRQPONMLKJIHGFEDCBA ) • zyxwvutsrqponmlkjihgfedcbaZYXWVUTSRQPONMLKJIHGFEDCBA per. Mov. Av (7. Native Forest)

  9. Forestry's concern Periodic sedimentation . At time of harvest and particularly earthworks. . Predominantly in small headwaters streams. II Exacerbated by historic plantings right to stream edge and or poor establishment layout relative to harvesting needs. . Second rotations should be better.

  10. Forestry's concern Periodic sedimentation • Highly erodible sedimentary Pakuratahi Study — Hawkes Bay formations. • Paired catchments — pastoral grazing (sheep) and S.Sediment Ratio% of Forest yield relative to Farm yield. plantation. 350% • Standard practice at the time. 300% • Peak during harvesting — 250% more specifically roading 200% earthworks. 150% • Declines quickly afterwards 100% • Overall sediment yield still 50% well down on pastoral 0% 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 landuse. —0—Ratio%

  11. So what does the industry do? Responsible operators should � NEW ZEALAND FOREST ROAD ENGINEERING MANUAL • Be working to Industry codes. • Increasing focus on good New Zealand Environmental Code of Practice planning and execution. for Plantation Forestry • Increasing focus on water — Voluntary setbacks on all streams... NZ FOREST OW NERS ASSOCI ATI ON I NC — 5m streams up to 3.0 wide. — 10m all larger streams. FOREST moms Vi Tr Trrar• tC• I thr, ASSOCI ATI ON — Sediment controls.

  12. Flood amelioration • Forests — Canopies intercept about 20% of rainfall in low - moderate rainfall events. — Root systems and low compaction allow rain infiltration. — Below about 30% clearance in an individual catchment, hydrological effects unlikely. — In very intense storms — _ moderation effect reduced. — Dryland environments or over- allocated water demand, plantations may reduce peak yield. PFOLSEN

  13. Biodiversity Terrestrial/ wetland reserves Fauna r zyxwvutsrqponmlkjihgfedcbaZYXWVUTSRQPONMLKJIHGFEDCBA � 1,1 le Gott. • Tawa/Podocarp/Hardwood 11C.I .VE0M'S FC5 � Prostrate KanAs • Manuka/kanuka/BroadleavedHW Phu.. * us • Adventive and exotic weeds & grasses 14.4 Med � • Tawa/ Broadleaved Hardwoods • Os,.,,, � • Lora, W al Bat ( OW .. I s) � Scandw radoha • Hardwood/Podocarp/beech Bbe Duct � erg W . eel � Savereve • Broadleaved Hardwood Shrub&fitmland Cassytha pauW ata � Long-W ed C.., � Spoutes Cw e 51nred zyxwvutsrqponmlkjihgfedcbaZYXWVUTSRQPONMLKJIHGFEDCBA ▪ Leptospermum/shrub HW/kowhai/podocarp Co:rearna aw osa � Lerapar. ( Rvul � sAaB Beech/Tawa/podocarp/harwood C000w a kroam I ts � Nero Zealand Fatal � Sw arm Mal. • • Subalpine mixed flax/shrubhardwood &tussock 0 ,0 0 s0 1 ,a * m .o. � Noet, bland aw n KW • Podocarp/Hardwood Dattha* � • Noon bind Kau • leptosperrnum/coprosma/flax wetland No.0, W ed KoW o � YhXw o • Beech Hard/Red dominant/ Podocarp Far. � Nor. bland Uncosolidated foredunes Gage 0.0 � NOT I sland MI A Warm lowland softwoods hardwoods • Rewarewa/Harcfwoods • Semi-wetland Sedge & femlands • Ouneland small leaved colonisers &grasses • Lowland Softwooditawa/titoki • Kahikatea/swampland • Geothermal vegetation • Exotic Species • Kahlkatea/matai/podocarp/HW • Blechnum Bracken or dense tree fern fernlands • • Manuka /Beech • Manuka /Hardwoods Lake /surface water wetland ▪ Geothermal sinter terraces • Gorse / nurse crop cover 1 0,600ha reserves = 19% ..,_ .4:— • ▪ • 7 t. PF Olsen FSC Group Scheme Certified Forests Map 1

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