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Page 1: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

V1-V7 ח ולידציה לדיגום"דו

18/10/2015

ayman
חוק חופש המידע
Page 2: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

i

תוכן עניינים

1 ........................................................................................................................................................ מנהלי סיכום

1 .................................................................................................................................... וניטור האתר פעילות

1 ........................................................................................................................................................ חריגות

2 ...................................................................................................................................................... הקדמה 1.0

3 ........................................................................................................ באתר הלוטים של עדכני וסטטוס מיקום 2.0

3.0 V1 – 5 .................................................................................................. הנחל במי המרחפים המוצקים כל סך

4.0 V2 – 6 .............................................................................................................. לנחל השחרור לפני השפך מי

6 ........................................................................................................................ (TSS) מרחפים מוצקים כ"סה

6 ........................................................................................................................................... (TN) כללי חנקן

6 ........................................................................................................................................... אמוניאקלי חנקן

TM ........................................................................................................................................ 7)) כללי מתכות

5.0 L3 – 8 .............................................................................................. בצנטרפוגות סחיטה לאחר גולמי סדימנט

L3 ................................................................................................................................................... 10 סיכום

6.0 L4 – 11 ....................................................................................... ביורמידיאציה לפני ערבוב לאחר סדימנט

L4 ................................................................................................................................................... 15 סיכום

7.0 L5– 16 .................................................................................... ביורמידיאציה במהלך ערבוב לאחר סדימנט

L5 ................................................................................................................................................... 16 סיכום

8.0 L6– 17 .................................................................................................. ביורמידיאציה לאחר מעורבב סדימנט

18 .......................................................................................................................................... יתסופ ולידציה 9.0

10.0 V7 - 19 ..................................................................................................................... חודשי אויר איכות ניטור

20 .............................................................................................................................. חריגים ניטור מאורעות 11.0

21 ...................................................................................................................................... האתר מפרט – 1 נספח

JONES ENVIRONMENTAL LABORATORY ................................................... 26 ממעבדת ולידציה חות"דו – 2 נפסח

רשימת טבלאות

1 ................................................................................................................... וניטור אתר פעילות סיכום: 1.01 טבלה

3 ......................................................................................................... באתר ים'הבאצ של עדכני סיכום: 2.01 טבלה

4 ............................................................................................ באתר ים'הבאצ ולידציית של עדכני סיכום: 2.02 טבלה

6 ............................................................................. (mg/l) השפך ערכי –( TSS) מרחפים מוצקים כ"סה: 4.01 טבלה

6 .......................................................... (mg/l) השפך ערכי סטטיסטיקת –( TSS) מרחפים מוצקים כ"סה: 4.02 טבלה

6 ................................................................................................................... (mg/l) השפך ערכי – TN: 4.03 טבלה

6 ................................................................................................ (mg/l) השפך ערכי סטטיסטיקת – TN: 4.04 טבלה

6 ................................................................................................................ (mg/l) השפך ערכי – NH3 :4.05 טבלה

6 .............................................................................................. (mg/l) השפך ערכי סטטיסטיקת – NH3: 4.06 טבלה

7 ................................................................................................................... (mg/l) השפך ערכי – TM: 4.07 טבלה

7 ................................................................................................(mg/l) השפך ערכי סטטיסטיקת – TM: 4.08 טבלה

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

ii 18/10/2015 רשות ניקוז ונחלים קישון

7 ...............................................................................................................................השפך ערכי – pH: 4.09 טבלה

8 ......................................................................................................... (S229-ו S228 וטל) מפורט TPH: 5.01 טבלה

8 ............................................................................................................ (S229-ו S228 וטל) כללי TPH: 5.02 טבלה

8 ........................................................................................................ (S229-ו S228 וטל) לחות ולתתכ: 5.03 טבלה

9 ................................................................................................................ (S229-ו S228 וטל) PAH’s: 5.04 טבלה

9 ............................................................................................................... (S229-ו S228 וטל) SVOC’s: 5.05 טבלה

10 .............................................................................. (S229-ו S228 וטל) PHENOLS & PHTHALATES : 5.06 טבלה

10 ........................................................................................................................... כללי מתכות -TM : 5.07 טבלה

11 .............................................................. (SP209 - ו SP225, SP228, SP227,SP226 יםלוט) כללי TPH: 6.02 טבלה

TM ................................................................................................................................................. 15: 6.09 טבלה

15 ......................................................................................................... תשטיפים – Leachable Metals:6.10 טבלה

16 ................................................................................................................ (SP166 לוט) מפורט TPH: 7.01 טבלה

16 .................................................................................................................... (SP166 לוט) כללי TPH: 7.02 טבלה

16 ................................................................................................................ (SP166 לוט) לחות תכולת: 7.03 טבלה

18 ........................................................ (SP228 -ו SP209 ,SP225,SP226,SP227 לוטים) סופית ולידציה: 9.01 טבלה

רשימת איורים

22 ........................................................................................................................................ ולידציה סכמת: 1 איור

23 ............................................................................................................................... הראשי האתר מפרט: 2 יורא

L4 ....................................................................................................................................... 24 - ו L3 מיקום: 3 איור

25 ........................................................................................................... (Windrows) הטיפול שורות מיקום: 4 איור

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פרוייקט חפירה וטיפול סדימנט נחל הקישון בועידוח ניטור ש

18/10/2015 1 רשות ניקוז ונחלים קישון

ום מנהלי סיכ

פעילות האתר וניטור 4/10/15 –פעילות האתר והניטור השבועית מסוכמת בטבלה המוצגת מטה, עבור התקופה בין ה

מסכמת את הפעילות היומית באתר כולל חפירה, שחרור מים 1.01. טבלה 17/10/2015 –עד ל

עולות הניטור ( ופעילות הצנטרפוגות )סחיטת בוצה(. בנוסף הטבלה מציגה את פLPPלנחל )

שהתבצעו על פי ימים בהתאם לפעילות האתר.

ח זה. "וסבר בדובאתר לניטור המבוצע ברמה היומית תכל אי התאמה בין הפעילות

וניטור אתר פעילות סיכום: 1.01 טבלה

. הדיגום 12/12/2014אינו מתרחש ברמה היומית מאז ( L3) לאחר סחיטה גולמי דיגום סדימנט

עקב תפוקה יומית נמוכה נדרשים מספר ימים להשלמת באצ' אצווה )באצ'( שלמה.נעשה עבור כל

L3. דיגום 1000m3)בממוצע כיומיים מלאים של פעילות חפירה(. נפח באצ' בודד אינו עולה מעל

לשלב העירבוב. תהקודם לערבוב, מתרחש כאשר באר מלאה )באצ' שלם( עובר

שעות ביממה, אלא אם ישנה חריגה 24שוטף של אספקת מי המיהול מבזן מאפשרים שחרור

מועברת לסחרור על מנת להגן על הביומסה כשאר אין חפירה מספר LPP-שבריכת האו בפרמטרים

הייתה LPP-רק במידה ובריכת ה .בפעילות החפירה יותר על כן השחרור אינו תלויימים רצופים,

ר לנחל. בסחרור כתוצאה מאי חפירה מתמשכת לא ייתרחש שחרו

(. בתוכנית העבודה בדרישות המכרז )וילונות כפולים הותקנו בנחל וילונות העומדים 22/6/2015 –ב

לא היו מותקנים וילונות העומדים 22/6/2015 –אמור להתבצע ברמה השבועית, עד ל V1דיגום

משיך התבצע ברמה יומית. לאחר התקנת הוילונות הדיגום ה V1בדרישת המכרז ועל כן דיגום

–להתבצע ברמה יומית על מנת לוודא כי אכן אין חריגות ברמת המוצקים המרחפים בנחל. החל מה

. יתבצע ברמה שבועית בהתאם לדרישת המכרז ותוכנית העבודה V1דיגום 5/7/2015

חריגות

3L – "בערכי תה חריגה אחתוהזח במהלך תקופת הדוTPH .

L4 – בערכי זוהו חריגותלא במהלך תקופת הדו"חTPH.

L5 – בערכי חריגות שתי זוהובמהלך תקופת הדו"חTPH.

Start EndDredger

Operation (V1)

LPP

Discharge

(V2)

Centrifuge

Operation (L3)V1 V2 L3

4/10/2015 No Yes Yes No No Yes

5/10/2015 No No No No No No

6/10/2015 No No No No No No

7/10/2015 No No No No No No

8/10/2015 No No No No No No

9/10/2015 No No No No No No

11/10/2015 No No No No No No

12/10/2015 No No No No No No

13/10/2015 No No No No No No

14/10/2015 No No No No No No

15/10/2015 No No No No No Yes

16/10/2015 No No No No No No

17/10/2015 No No No No No No

TOTAL DAYS 0 1 1 0 0 2

Date

Site Activities Validation TestingDredging Time

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 2 וןרשות ניקוז ונחלים קיש

V1-V7 דוח ולידציה לדיגום

הקדמה 1.0

.17/10/2015 - 4/10/2015דוח זה מסכם את תוצאות הולידציה סדימנט ומים עבור התקופה

פה זו היא . מטרת פעילות האתר במהלך תקוK3789 – K3781טווח הדגימות בדוח מצויות ב

.A2 –ו A1 קרקע שמקורה בבריכותו ביורמדיאציה של הסדימנט הנחפר מקרקעית נחל הקישון

הדיגום נעשה במספר אתרים הן בתוך האתר והן במספר נקודות בנחל עצמו. את מיקום נקודות

תוצאות הדיגום מוצגות בטבלאות, כאשר .1בנספח אזור הטיפול בקרקע ניתן לראות והדיגום

במידה וישנן חריגות הן מצויינות, במידה וננקטו אמצעים להתמודדות עם החריגות יופיע תיאור

שלהם.

בטבלאות, חריגות מודגשות באדום בעוד שנתונים העומדים בתקנים מופיעים בירוק. במידה ומזוהה

חריגה בממוצע אך לא בערכים המקסימאליים, זו תופיע בכתום.

ם לשיטות המוצהרות. דיגום הולידציה שהתבצע המהלך תקופת הו"ח כל הדיגום נעשה בהתא

מפורט מטה:

L3 – סדימנט גולמי לאחר סחיטה בצנטרפוגות;

4L – ( לפני ביורמידיאציה חול –גזם ואנאורגני –סדימנט לאחר ערבוב )תוספת של חומר אורגני;

L5 – סדימנט לאחר ערבוב במהלך ביורמידיאציה;

V7 – איכות אויר חודשי ניטור

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 3 וןרשות ניקוז ונחלים קיש

מיקום וסטטוס עדכני של הלוטים באתר 0.0

מסכמת את הסטטוס של באצ'ים של קרקע המצויים באתר נכון לעת הגשת ד"ח זה, 2.01טבלה

הם באצ'ים יעודיים עבור S3-ו S2באצ'ים שלב הדחיסה. עד להחל משלב הסחיטה, שלב הטיפול ו

באצ'ים הם של סדימנט בשלבים שונים. , כל יתר הV2-ו V1דגימות

באתר ים'הבאצ של עדכני סיכום :2.01 טבלה

לא מצטבר חול, החול שנוצר נצרך ישירות לערבוב לתוך הסדימנט. 1/3/2015-מאז ה

אל אזור דחיסת הגבהות לאחר שעבר ומוזג SP228-וS218,SP221,SP222,,SP223 S227 יםבאצ'

ולידציה מלאה.

Lot/Batch Location StatusEstimated

Quantity - m3

Number

of

Samples

Notes

S2 Reports Only Varying Data N/A 2276 V1 TSS Data

S3 Reports Only Varying Data N/A 794 V2 Efflluent Data

S58

Test Pads-

Landscape /

Storage Area

Below Validation

Thresholds154953 534

Contains S1,S4,S5,S6,S7,S8,S9,S10,S11,S12,S13,

S14,S15,S16,S17,S19,S20,S21,S22,S24,S25,S26,S27,S29,S30,S31,S32,S33,S34,S35,S36,

S37,S38,S39,S40,S41,S42,S43,S44,S45,S46,S47,S49,S50,S51,S52,S53,S54,S55,S56,S57,

S59,S60,S61,S62,S63,S64,S65,S66,S67,S68,S69,S70,S71,S72,S73,S74,S75,S76,S77,S78,

S79,S80,S81,S82,S83,S84,S85,S86,S87,S88,S89,S90,S91,S93,S94,S95,S96,S97,S98,S99,

S100,S101,S102,S103,S104,S105,S106,S107,S108,S109,S110,S111,S112,S113,S114,S11

5,S116,S117,S118,S119,S120,S121,S122,S123,S124,S125,S126,S127,S128,S129,S130,S

131,S132,S133,S134,S135,S137,S138,SP139,SP140,SP141,SP142,SP143,SP144,SP145,S

146,S148,SP151,SP152,SP153,SP154,SP155,SP156,S157,S158,SP159,SP160,SP161,SP1

62,SP163,SP164,S165,SP171,SP172,SP173,S174,SP177,SP178,SP179,SP180,SP181,

S182,SP183,S184,SP185,

S186,S187,S188,S189,S190,SP191,SP192,SP193,SP194,SP195,SP196,S197,SP198,

SP199,SP200,S201,SP202,SP204,S205,S207,SP212,SP213,SP214,SP215,SP216,SP217,S

218,SP219,SP221,S222,SP223,S227 and SP228

S92 22 River Core Samples

SP147 PAD 2Above Validation

Thresholds3248 11 S136, S150 and S170

SP166 PAD 6Above Validation

Thresholds915 8 S208 (300 m3)

SP167 PAD 6Above Validation

Thresholds1150 3

SP168 PAD 5Above Validation

Thresholds1020 5

SP169 PAD 4Above Validation

Thresholds640 6 S182 (220m3)

SP206 PAD 3Below Validation

Thresholds1120 1

SP209 PAD 2Below Validation

Thresholds1800 1

SP211 PAD 4Below Validation

Thresholds1020 1

SP225 PAD 3Below Validation

Thresholds900 1

S229 PAD 1Below Validation

Thresholds3000 1

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ייקט חפירה וטיפול סדימנט נחל הקישוןפרו דוח ניטור שבועי

18/10/2015 4 רשות ניקוז נחלים קישון

באתר ים'הבאצ ולידציית של עדכני סיכום :2.02 טבלה

Lot/Batch Relevant K-numberFinal Validation

Sample IDNotes

S58

2,K16,K25,K30,K35,K40,K47,K68,K76,K82,K93,K114,K115,K121,K132,K153,K169,K175,K186,K192,K208,K219,K225,K241,K242,K248,K249,K269,

K286,K297,K298,K299,K320,K331,K342,K343,K354,K365,K366,K367,K388,K399,K400,K401,K412,K434,K435,K436,K447,K448,K459,K470,K482,

K483,K484,K495,K506,K527,K528,K529,K540,K541,K542,K543,K544,K545,K561,K562,K578,K579,K580,K581,K582,K583,K614,K615,K616,K632,

K633,K634,K635,K651,K652,K653,K669,K670,K671,K688,K689,K690,K706,K707,K708,K709,K710,K711,K712,K743,K744,K745,K746,K762,K763,

K764,K766,K767,K771,K772,K773,K774,K775,K776,K777,K793,K795,K811,K812,K828,K829,K845,K846,K862,K863,K879,K880,K881,K882,K898,

K914,K930,K946,K947,K948,K964,K965,K981,K997,K1014,K1048,K1064,K1013,K1015,K1046,K1047,K1080,K1106,K1132,K1133,K1159,K1160,K

1180,K1181,K1193,K1194,K1202,K1213,K1267,K1268,K1231,K1232,K1250,K1251,K1286,K1287,K1309,K1310,K1326,K1327,K1345,K1346,K134

7,K1348,K1367,K1368,K1387,K1386,K1405,K1406,K1424,K1442,K1443,K1444,K1462,K1476,K1477,K1483,K1489,K1490,K1491,K1522,K1538,K

1539,K1540,K1551,K1558,K1559,K1575,K1576,K1592,K1598,K1599,K1600,K1601,K1607,K1623,K1624,K1625,K1641,K1657,K1658,K1664,K166

5,K1666,K1682,K1683,K1684,K1685,K1701,K1707,K1723,K1739,K1740,K1741,K1742,K1758,K1759,K1760,K1761,K1762,K1778,K1779,K1785,K

1786,K1802,K1803,K1804,K1805,K1806,K1807,K1818,K1819,K1820,K1821,K1822,K1823,K1824,K1835,K1841,K1842,K1858,K1859,K1860,K187

8,K1895,K1896,K1897,K1903,K1904,K1905,K1906,K1917,K1918,K1939,K1940,K1941,K1942,K1953,K1954,K1955,K1961,K1962,K1963,K1969,K

1970,K1971,K1972,K1988,K1989,K2005,K2006,K2007,K2023,K2024,K2040,K2041,K2072,K2073,K2074,K2075,K2081,K2097,K2113,K2114,K211

5,K2141,K2142,K2143,K2149,K2165,K2166,K2167,K2183,K2189,K2190,K2191,K2192,K2208,K2209,K2210,K2211,K2212,K2213,K2229,K2230,K

2231,K2262,K2263,K2274,K2275,K2287,K2301,K2302,K2323,K2324,K2325,K2336,K2337,K2348,K2359,K2360,K2361,K2362,K2390,K2421,K242

2,K2423,K2434,K2465,K2502,K2503,K2514,K2567,K2589,K2590,K2616,K2637,K2638,K2639,K2670,K2671,K2692,K2693,K2714,K2725,K2726,K

2742,K2743,K2764,K2765,K2766,K2767,K2778,K2789,K2800,K2821,K2822,K2833,K2844,K2865,K2867,K2887,K2898,K2909,K2920,K2931,K293

7,K2938,K2949,K2960,K2961,K2962,K2963,K2964,K2975,K2986,K2987,K3018,K3019,K3030,K3041,K3042,K3043,K3044,K3065,K3066,K3077,K

3088,K3089,K3100,K3100,K3101,K3102,K3103,K3114,K3141,K3152,K3163,K3163,K3185,K3186,K3187,K3188,K3189,K3190,K3201,K3211,K322

3,K3266,K3267,K3268,K3276,K3289,K3290,K3291,K3292,K3293,K3294,K3295,K3297,K3323,K3335,K3336,K3337,K3359,K3370,K3371,K3372,K

3388,K3389,K3390,K3391,K3392,K3404,K3405,K3406,K3408,K3419,K3430,K3403,K3407,K3431,K3432,K3434,K3435,K3436,K3437,K3453,K345

4,K3455,K3456,K3458,K3459,K3461,K3462,K3463,K3464,K3465,K3466,K3467,K3478,K3479,K3494,K3495K3496,K3529,K3542,K3543,K3544,K3

559,K3562,K3577,K3578,K3579,K3580,K3581,K3582,K3583,K3584,K3585,K3586,K3587,K3589,K3601,K3602,K3603,K3604,K3605,K3606,K3626

,K3702,K3717,K3718,K3729,K3730,K3731,K3732,K3733,K3734,K3735,K3736,K3752,K3753,K3780,K3781,K3782,K3783,K3786

K35,K47,K115,K169,K186,K208,K242,K297,K298,K29

9,K366,K367,K401,K434,K448,K481,K482,K483,K543,

K544,K632,K669,K706,K709,K746,K812,K829,K846,K

863,K880,K881,K882,K947,K948,K965,K1013,K1014,

K1046,K1106,K1133,K1160,K1194,K1232,K1250,K12

67,K1287,K1327,K1346,K1347,K1387,K1406,K1442,K

1444,K1477,K1483,K1490,K1538,K1558,K1601,K162

4,K1658,K1664,K1665,K1683,K1742,K1786,K1807,K1

818,K1841,K1842,K1895,K1939,K1940,K1963,K1969,

K1970,K2006,K2041,K2081,K2141,K2166,K2190,K21

91,K2209,K2213,K2263,K2274,K2301,K2302,K2323,K

2325,K2360,K2390,K2421,K2423,K2434,K2502,K251

4,K2589,K2590,K2637,K2639,K2671,K2693,K2726,K2

743,K2766,K2778,K2789,K2822,K2833,K2865,K2887,

K2909,K2960,K2962,K2963,K2986,K3018,K3019,K30

41,K3043,K3064,K3077,K3089,K3101,K3103,K3141,K

3163,K3189,K3276,K3290,K3291,K3293,K3294,K329

5,K3335,K3336,K3359,K3370,K3372,K3389,K3390,K3

391,K3404,K3406,K3434,K3435,K3437,K3453,K3458,

K3459,K3461,K3462,K3463,K3464,K3465,K3466,K34

67,K3544,K3494,K3495,K3496,K3543,K3544,K3577,K

3578,K3580,K3581,K3582,K3584,K3585,K3589,K360

1,K3602,K3603,K3604,K3605,K3606,K3626,K3718,K3

729,K3730,K3731,K3732,K3733,K3734,K3735,K3736,

K3753,K3782,K3783,K3786

ContainsS1,S4,S5,S6,S7,S8,S9,S10,S11,S12,

S13,S14,S15,S16,S17,S19,S20,S21,S22,S24,S25,S26,

S27,S29,S30,S31,S32,S33,S34,S35,S36,S37,S38,S39,

S40,S41,S42,S43,S44,S45,S46,S47,S49,S50,S51,S52,

S53,S54,S55,S56,S57,S59,S60,S61,S62,S63,S64,S65,

S66,S67,S68,S69,S70,S71,S72,S73,S74,S75,S76,S77,

S78,S79,S80,S81,S82,S83,S84,S85,S86,S87,S88,S89,

S90,S91,S93,S94,S95,S96,S97,S98,S99,S100,S101,S1

02,S103,S104,S105,S106,S107,S108,S109,S110,S11

1,S112,S113,S114,S115,S116,S117,S118,S119,S120,

S121,S122,S123,S124,S125,S126,S127,S128,S129,S

130,S131,S132,S133,S134,S135,S137,S138,SP139,S

P140,SP141,SP142,SP143,SP144,SP145,S146,SP148

,SP151,SP152,SP153,SP154,SP155,SP156,S157,S158

,SP159,SP160,SP161,SP162,SP163,SP164,S165,SP17

1,SP172,SP173,SP174,SP175,SP176,SP177,S178,SP1

79,SP182,SP183,S184,SP185,S186,S187,S188

,S189,S190,SP191,SP192,SP193,SP194,SP195,S196,

S197,SP198,SP199,SP200,S201,SP202,SP203,SP204,

S205,SP207,S208,S210,SP212,SP213,SP214,SP215,S

P216,SP217,SP218,S219,SP220,SP221,SP222,SP223

,S224,S226,SP227 and SP228

S92 K2288-K2300 River Core Samples.

SP147 K3234,K3235,K3358,K3334,K3433,K3492,K3493,K3530,K3531,K3560,K3561 S136, S150,S170

SP166 K3480,K3545,K3563,K3614,K3628,K3629,K3630,K3631,K3703,K3704,K3705,K3706,K3754,K3755,K3784,K3785 S208 (300 m3)

SP167 K3481,K3456,K3564

SP168 K3460,K3527,K3557,K3566,K3612

SP169 K3436,K3457,K3528,K3558,K3565,K3613 S182

SP206 K3588

SP209 K3788

SP211 K3625 S224 S226

SP225 K3787 S226

S229 K3789

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 5 רשות ניקוז נחלים קישון

0.0 V1 – סך כל המוצקים המרחפים במי הנחל

בנחל. TSSת ובדיק התבצעה חפירה ממושכתולכן לא התבצעו בתקופת הדו"ח לא

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 6 רשות ניקוז נחלים קישון

0.0 V2 – מי השפך לפני השחרור לנחל

צטבר על הערכים הממוצעים . דו"ח זה מציג מידע מV2נלקחה דוגמת לא במהלך תקופת דו"ח זה

שנלקחו מתחילת הפרוייקט. V2 –והמקסימאליים של דוגמאות ה

(TSSמוצקים מרחפים )סה"כ

(mg/l) השפך ערכי –( TSS) מרחפים מוצקים כ"סה: 4.01 טבלה

(mg/l) השפך ערכי סטטיסטיקת –( TSS) מרחפים מוצקים כ"סה : 4.02 טבלה

(TNחנקן כללי )

(mg/l) השפך ערכי – TN: 4.03 טבלה

(mg/l) השפך ערכי סטטיסטיקת – TN :4.04 טבלה

חנקן אמוניאקלי

(mg/l) השפך ערכי – NH3 :4.05 טבלה

(mg/l) השפך ערכי סטטיסטיקת – NH3: 4.06 טבלה

Parameter MaximumDate

MaximumMinimum

Date

MinimumAverage Threshold

TSS 313 31/03/2014 10 27/12/2014 68.38 200

Parameter MaximumDate

MaximumMinimum

Date

MinimumAverage Threshold

TN 29.6 28/10/2014 3.4 16/11/2014 15.81 20

Parameter MaximumDate

MaximumMinimum

Date

MinimumAverage Threshold

Amm. N 17.14 29/07/2014 0.23 26/10/2014 2.82 5

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18/10/2015 7 רשות ניקוז נחלים קישון

TM)מתכות כללי ) (mg/l) השפך ערכי – TM: 4.07 טבלה

(mg/l) השפך רכיע סטטיסטיקת – TM: 4.08 טבלה

NB - Please note the numbers above are calculated by taking any result indicated as being <limit of detection (LOD) as the actual result, implying the maximum, minimum and average values or conservatively high, and in reality may

well be below the values indicated above.

(pHערך הגבה )

השפך ערכי – pH: 4.09 טבלה

Parameter Maximum Minimum AverageTotal Antimony 0.00700 0.00200 0.00214

Total Arsenic 0.02560 0.00250 0.00426

Total Beryllium 0.00060 0.00050 0.00047

Total Cadmium 0.00150 0.00050 0.00049

Total Chromium 0.01730 0.00150 0.00264

Total Cobalt 0.00500 0.00200 0.00193

Total Copper 0.00800 0.00700 0.00662

Total Lead 0.01800 0.00500 0.00503

Total Manganese 0.69200 0.01500 0.14504

Total Nickel 0.02600 0.00200 0.00303

Total Selenium 0.04500 0.00300 0.01389

Total Thallium 0.00400 0.00300 0.00284

Total Vanadium 0.03410 0.00150 0.00611

Total Zinc 1.01800 0.01000 0.12703

Mercury Total by CVAF 0.00005 0.00001 0.00001

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 8 רשות ניקוז נחלים קישון

5.0 L3 – סדימנט גולמי לאחר סחיטה בצנטרפוגות

מוצגות מטה. התוצאות S229 -ו S228 ים'עבור באצ L3 ותאדוגמ 2ו הלך תקופת הדו"ח נאספבמ

(S229-ו S228וט ל) מפורט TPH: 5.01 טבלה

(S229-ו S228וט ל) כללי TPH: 5.02 בלהט

(S229-ו S228וט ל) לחות תכולת: 5.03 טבלה

Sample ID Description Sampled Date >C5-C6 >C6-C8 >C8-C10 >C10-C12 >C12-

C16

>C16-

C21 >C21-C35 >C35-C44 Total

K3781 Cake 10/04/2015 <0.1 0.6 5.6 197.9 570 446 1087 178 2485

K3789 Cake 15/10/2015 <0.1 <0.1 1.3 9 31 32 76 11 160

Aliphatics (mg/kg)

Sample ID Description Sampled Date >EC5-EC7 >EC7-EC8 >EC8-EC10 >EC10-EC12 >EC12-

EC16

>EC16-

EC21

>EC21-

EC35

>EC35-

EC44Total

K3781 Cake 10/04/2015 <0.1 <0.1 0.6 <0.2 33 137 564 77 812

K3789 Cake 15/10/2015 <0.1 <0.1 <0.1 <0.2 <4 <7 34 <7 34

Aromatics (mg/kg)

Sample ID Lot/ Batch DescriptionTotal aliphatics and

aromatics (C5-44)Threshold

K3781 S228 Cake 3297 1,560

K3789 S229 Cake 194 1,560

TOTAL TPH (mg/kg)

Sample ID Lot/ Batch Description Moisture Content %

K3781 S228 Cake 66.3

K3789 S229 Cake 28.7

Moisture Content %

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18/10/2015 9 רשות ניקוז נחלים קישון

(S229-ו S228וט ל) PAH’s: 5.04 טבלה

(S229-ו S228וט ל) SVOC’s: 5.05 טבלה

Sample ID K3781 K3789

Lot/ Batch S228 S229

Description Cake Cake

Date 10/04/2015 15/10/2015

2-Chloronaphthalene <0.01 <0.01 681,000

2-Methylnaphthalene 0.13 <0.01 34,100

Naphthalene <0.01 <0.01 2.34

Acenaphthylene <0.01 <0.01 235,000

Acenaphthene <0.01 <0.01 223,000

Fluorene 0.03 <0.01 149,000

Phenanthrene 0.14 0.02 117,000

Anthracene <0.01 <0.01 1,120,000

Fluoranthene <0.01 <0.01 149,000

Pyrene 0.04 0.02 112,000

Benzo(a)anthracene <0.01 <0.01 350

Chrysene <0.01 <0.01 35,700

Benzo(bk)fluoranthene <0.01 <0.01 357

Benzo(a)pyrene <0.01 <0.01 36

Indeno(123cd)pyrene <0.01 <0.01 357

Dibenzo(ah)anthracene <0.01 <0.01 36

Benzo(ghi)perylene <0.01 <0.01 117,000

PAH's (mg/kg)

Threshold

Sample ID K3781 K3789

Lot/ Batch S228 S229

Description Cake Cake

Date 10/04/2015 15/10/2015

1,2-Dichlorobenzene <0.01 <0.01 303

1,2,4-Trichlorobenzene <0.01 <0.01 881

1,3-Dichlorobenzene <0.01 <0.01 4,300

1,4-Dichlorobenzene <0.01 <0.01 584

2-Nitroaniline <0.01 <0.01 5.35

2,4-Dinitrotoluene <0.01 <0.01 1,500

2,6-Dinitrotoluene <0.01 <0.01 0.349

3-Nitroaniline <0.01 <0.01 12,000

4-Bromophenylphenylether <0.01 <0.01 339

4-Chloroaniline <0.01 <0.01 12,800

4-Chlorophenylphenylether <0.01 <0.01 0.169

4-Nitroaniline <0.01 <0.01 17,600

Azobenzene <0.01 <0.01 8,520

Bis(2-chloroethoxy)methane <0.01 <0.01 0.374

Bis(2-chloroethyl)ether <0.01 <0.01 0.194

Carbazole <0.01 <0.01 0.19

Dibenzofuran <0.01 <0.01 0.568

Hexachlorobenzene <0.01 <0.01 2,000,000

Hexachlorobutadiene <0.01 <0.01 0.626

Hexachlorocyclopentadiene <0.01 <0.01 4.87

Hexachloroethane <0.01 <0.01 n/a

Isophorone <0.01 <0.01 n/a

N-nitrosodi -n-propylamine <0.01 <0.01 n/a

Nitrobenzene <0.01 <0.01 n/a

Threshold

SVOCS (mg/kg)

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18/10/2015 10 רשות ניקוז נחלים קישון

(S229-ו S228וט ל) PHENOLS & PHTHALATES : 5.06 טבלה

כללי מתכות -TM : 5.07 טבלה

יוצגו בדו"חות הבאים, כאשר S229 –ו S208 S226,, S228, SP227לבאצ'ים TMתוצאות עבור

.Jones UK –התוצאות ייתקבלו מ

L3סיכום

.4/10/2015 ךכללי בתארי TPHבערכי ה אחתחריג הנרשמבמהלך תקופת הדו"ח

Sample ID K3781 K3789

Lot/ Batch S228 S229

Description Cake Cake

Date 10/04/2015 15/10/2015

Phenols

2-Chlorophenol <0.01 <0.01 42,600

2-Methylphenol <0.01 <0.01 190,000

2-Nitrophenol <0.01 <0.01 11,400

2,4-Dichlorophenol <0.01 <0.01 12,800

2,4-Dimethylphenol <0.01 <0.01 85,600

2,4,5-Trichlorophenol <0.01 <0.01 428,000

2,4,6-Trichlorophenol <0.01 <0.01 4,280

4-Chloro-3-methylphenol <0.01 <0.01 428,000

4-Methylphenol <0.01 <0.01 21,200

4-Nitrophenol <0.01 <0.01 8,560

Pentachlorophenol <0.01 <0.01 429

Phenol <0.01 <0.01 470,000

Phthalates

Bis(2-ethylhexyl) phthalate 16.06 2.62 21,400

Butylbenzyl phthalate <0.01 <0.01 158,000

Di-n-butyl phthalate 0.08 <0.01 428,000

Di-n-Octyl phthalate <0.01 <0.01 180,000

Diethyl phthalate <0.01 <0.01 3,420,000

Dimethyl phthalate <0.01 <0.01 3,600,000

PHENOLS & PHTHALATES (mg/kg)

Threshold

Sample ID K3562 K3717

Lot/ Batch S190 S224

Description Cake Cake

Date 13/8/2015 20/9/2015

Aluminium 57170 47830 8,390,000

Antimony <1 <1 25

Arsenic 43 31.4 110

Beryllium 2.1 1.7 93

Cadmium 13.2 14.7 64

Chromium 138 119.6 999

Cobalt 16.5 13.9 2,550

Copper 128 120 613

Iron 47310 38950 5,960,000

Lead 36 28 160

Manganese 614 330 21,400

Nickel 56 51.7 305

Selenium 1 <1 9

Thallium <1 <1 85.2

Titanium 1400 1268 12,800,000

Vanadium 129 114 174

Zinc 443 460 3,720

Mercury CVAF <0.5 <0.5 n/a

Hexavalent

Chromium<0.3 <0.3 3,850

Threshold

TOTAL METALS (mg/kg)

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18/10/2015 11 רשות ניקוז נחלים קישון

6.0 L4 – לאחר ערבוב לפני ביורמידיאציהסדימנט

. SP209-ו SP225 ,SP226,SP227,SP228אספו במהלך תקופת דו"ח זה עבור באצ'יםנ L4דגימות שחמ

סימון באצ'ים: עבור באצ'ים חדשים שיפתחו לחומר שמקורו בחפירת הנחל הקידומת תמשיך להיות

S# עבור באצ'ים יעודיים לחומר שמגיע מהבריכות הישנות הקידומת תהיה ,SP# .

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) מפורט TPH: 6.01 טבלה

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) כללי TPH: 6.02 טבלה

* TPH Average- 1150 מעל הוא שגודלם ים'באצ עבורm3 ,1150 כל עבורm3 מורכבת דוגמא נאספת .הנתון' לבאצ הדוגמאות כל ןבי ממוצע על מבוסס הדוגמא של TPH – ה תכולת של הסופי הערך ועל

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) pH: 6.03 טבלה

Sample IDLot/

BatchDescription

Sampled

Date>C5-C6 >C6-C8 >C8-C10

>C10-

C12

>C12-

C16

>C16-

C21

>C21-

C35

>C35-

C44Total

K3782 S226 Cake 10/06/2015 <0.1 0.2 2.6 25.4 93 75 163 31 390

K3783 S227 Cake 10/06/2015 <0.1 0.6 4.5 48 164 120 280 26 643

K3786 S228 Cake 10/11/2015 <0.1 1.6 2.9 67 183 149 507 55 966

K3787 SP225 Soil 10/12/2015 <0.1 <0.1 <0.1 <0.2 <4 <7 35 <7 35

K3788-1 SP209 Soil 13/10/2015 <0.1 <0.1 <0.1 0.9 26 86 207 30 350

K3788-2 SP209 Soil 13/10/2015 <0.1 <0.1 <0.1 <0.2 19 64 157 23 263

Aliphatics (mg/kg)

Sample IDLot/

BatchDescription

Sampled

Date>EC5-EC7 >EC7-EC8

>EC8-

EC10

>EC10-

EC12

>EC12-

EC16

>EC16-

EC21

>EC21-

EC35

>EC35-

EC44Total

K3782 S226 Cake 10/06/2015 <0.1 <0.1 0.2 <0.2 21 46 115 <7 182

K3783 S227 Cake 10/06/2015 <0.1 <0.1 0.4 <0.2 18 49 195 <7 262

K3786 S228 Cake 10/11/2015 <0.1 <0.1 0.2 <0.2 39 88 403 61 591

K3787 SP225 Soil 10/12/2015 <0.1 <0.1 <0.1 <0.2 <4 <7 36 <7 36

K3788-1 SP209 Soil 13/10/2015 <0.1 <0.1 <0.1 <0.2 <4 21 117 18 156

K3788-2 SP209 Soil 13/10/2015 <0.1 <0.1 <0.1 <0.2 <4 20 121 25 166

Aromatics mg/kg

Sample ID Lot/ Batch Description Sampled DateTotal aliphatics and

aromatics (C5-44)

Total TPH

average Threshold

K3782 S226 Cake 10/06/2015 572 - 1560

K3783 S227 Cake 10/06/2015 905 - 1560

K3786 S228 Cake 10/11/2015 1557 - 1560

K3787 SP225 Soil 10/12/2015 71 - 1560

K3788-1 SP209 Soil 13/10/2015 506 1560

K3788-2 SP209 Soil 13/10/2015 429 1560

TOTAL TPH (mg/kg)

468

K3782 K3783 K3786 K3787 K3788-1 K3788-2

S226 S227 S228 SP225 SP209 SP209

Cake Cake Cake Soil Soil Soil

10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015

pH 7.22 7.12 7.38 8.03 7.81 7.76 7.0 - 8.5

Threshold

Range

pH

Parameter

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 12 רשות ניקוז נחלים קישון

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) לחות תכולת: 6.04 טבלה

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) VOC’s: 6.05 טבלה

K3782 K3783 K3786 K3787 K3788-1 K3788-2

S226 S227 S228 SP225 SP209 SP209

Cake Cake Cake Soil Soil Soil

10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015

Moisture Content 41.6 50.7 49.1 16.4 14.7 14.7

Parameter

Moisture Content %

K3782 K3783 K3786 K3787 K3788-1 K3788-2

S226 S227 S228 SP225 SP209 SP209

Cake Cake Cake Soil Soil Soil

10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015

Dichlorodif luoromethane <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 0.672

Methy l Tertiary Buty l Ether <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 2.4

Chloromethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 1.14

Vinyl Chloride <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 0.00587

Bromomethane <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.0897

Chloroethane <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 165

Trichlorofluoromethane <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 7.45

1,1-Dichloroethene (1,1 DCE) <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 2.71

Dichloromethane (DCM) <0.007 <0.007 <0.007 <0.007 <0.007 <0.007 0.298

trans-1-2-Dichloroethene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 4.14

1,1-Dichloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0803

cis-1-2-Dichloroethene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 17,000

2,2-Dichloropropane <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.503

Bromochloromethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 5.16

Chloroform <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.00893

1,1,1-Trichloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 146

1,1-Dichloropropene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0237

Carbon tetrachloride <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.011

1,2-Dichloroethane <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.0249

Benzene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.055

Trichloroethene (TCE) <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0809

1,2-Dichloropropane <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 0.0466

Dibromomethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 1.28

Bromodichloromethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0127

cis-1-3-Dichloropropene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 2.96

Parameter Threshold

VOC (mg/kg)

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 13 רשות ניקוז נחלים קישון

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) VOC’s: 6.05 טבלה

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) PHENOLS & PHTHALATES: 6.06 טבלה

K3782 K3783 K3786 K3787 K3788-1 K3788-2

S226 S227 S228 SP225 SP209 SP209

Cake Cake Cake Soil Soil Soil

10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015

Toluene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 1,170

trans-1-3-Dichloropropene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.108

1,1,2-Trichloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.106

Tetrachloroethene (PCE) <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0319

1,3-Dichloropropane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 170,000

Dibromochloromethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0703

1,2-Dibromoethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.00387

Chlorobenzene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 26.5

1,1,1,2-Tetrachloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.147

Ethylbenzene 0.021 0.059 0.041 <0.003 <0.003 <0.003 0.486

p/m-Xylene 0.022 0.077 0.059 <0.006 <0.006 <0.006 43.9

o-Xylene 0.007 0.032 0.024 <0.003 <0.003 <0.003 54

Styrene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 1,140

Bromoform <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 2.57

Isopropylbenzene 0.012 0.028 0.022 <0.003 <0.003 <0.003 201

1,1,2,2-Tetrachloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.135

Bromobenzene <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 53.7

1,2,3-Trichloropropane <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.916

Propylbenzene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 641

2-Chlorotoluene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 170,000

1,3,5-Trimethylbenzene <0.003 0.043 <0.003 <0.003 <0.003 <0.003 85,200

4-Chlorotoluene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 170,000

tert-Butylbenzene <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 426,000

1,2,4-Trimethylbenzene 0.029 0.114 0.110 <0.006 <0.006 <0.006 5.73

sec-Butylbenzene <0.004 0.026 <0.004 <0.004 <0.004 <0.004 426,000

4-Isopropyltoluene 0.034 0.162 0.108 <0.004 <0.004 <0.004 1,060,000

1,3-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 2.18

1,4-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.36

n-Butylbenzene <0.004 0.148 0.116 <0.004 <0.004 <0.004 426,000

1,2-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 355

1,2-Dibromo-3-chloropropane <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.00593

Hexachlorobutadiene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.202

1,2,3-Trichlorobenzene <0.007 <0.007 <0.007 <0.007 <0.007 <0.007 3,420

Parameter Threshold

VOC (mg/kg)

Parameter K3782 K3783 K3786 K3787 K3788-1 K3788-2

Lot/ Batch S226 S227 S228 SP225 SP209 SP209

Description Cake Cake Cake Soil Soil Soil

Date 10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015

Phenols

2-Chlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 42,600

2-Methylphenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 190,000

2-Nitrophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 11,400

2,4-Dichlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 12,800

2,4-Dimethylphenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 85,600

2,4,5-Trichlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 428,000

2,4,6-Trichlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 4,280

4-Chloro-3-methylphenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 428,000

4-Methylphenol <0.01 <0.01 0.04 <0.01 <0.01 <0.01 21,200

4-Nitrophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 8,560

Pentachlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 429

Phenol <0.01 0.6 <0.01 <0.01 <0.01 <0.01 470,000

Phthalates

Bis(2-ethylhexyl) phthalate 7.47 10.82 1.52 <0.01 1.11 1.34 21,400

Butylbenzyl phthalate <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 158,000

Di-n-butyl phthalate 0.03 0.03 <0.01 <0.01 <0.01 <0.01 428,000

Di-n-Octyl phthalate <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 180,000

Diethyl phthalate <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 3,420,000

Dimethyl phthalate <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 3,600,000

Threshold

PHENOLS & PHTHALATES (mg/kg)

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 14 רשות ניקוז נחלים קישון

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) PAH’s: 6.07 טבלה

(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) SVOC’s: 6.08 טבלה

Sample ID K3782 K3783 K3786 K3787 K3788-1 K3788-2

Lot/ Batch S226 S227 S228 SP225 SP209 SP209

Description Cake Cake Cake Soil Soil Soil

Date 10/06/2015 10/11/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015

2-Chloronaphthalene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 681,000

2-Methylnaphthalene 0.03 0.07 0.04 <0.01 <0.01 0.01 34,100

Naphthalene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 2.34

Acenaphthylene <0.01 <0.01 <0.01 <0.01 <0.01 0.02 235,000

Acenaphthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 223,000

Fluorene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 149,000

Phenanthrene 0.04 0.07 0.05 <0.01 0.02 0.03 117,000

Anthracene <0.01 <0.01 <0.01 <0.01 <0.01 0.01 1,120,000

Fluoranthene <0.01 <0.01 <0.01 <0.01 0.02 0.02 149,000

Pyrene <0.01 0.03 0.02 0.02 0.04 0.05 112,000

Benzo(a)anthracene <0.01 <0.01 <0.01 0.05 0.03 0.04 350

Chrysene <0.01 <0.01 <0.01 <0.01 0.03 0.04 35,700

Benzo(bk)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 357

Benzo(a)pyrene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 36

Indeno(123cd)pyrene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 357

Dibenzo(ah)anthracene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 36

Benzo(ghi)perylene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 117,000

Threshold

PAH's (mg/kg)

K3782 K3783 K3786 K3787 K3788-1 K3788-2

S226 S227 S228 SP225 SP209 SP209

Cake Cake Cake Soil Soil Soil

10/06/2015 10/11/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015

1,2-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 303

1,2,4-Trichlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 881

1,3-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 4,300

1,4-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 584

2-Nitroaniline <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 5.35

2,4-Dinitrotoluene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 1,500

2,6-Dinitrotoluene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.349

3-Nitroaniline <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 12,000

4-Bromophenylphenylether <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 339

4-Chloroaniline <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 12,800

4-Chlorophenylphenylether <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.169

4-Nitroaniline <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 17,600

Azobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 8,520

Bis(2-chloroethoxy)methane <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.374

Bis(2-chloroethyl)ether <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.194

Carbazole <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.19

Dibenzofuran <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.568

Hexachlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 2,000,000

Hexachlorobutadiene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.626

Hexachlorocyclopentadiene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 4.87

Hexachloroethane <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 n/a

Isophorone <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 n/a

N-nitrosodi -n-propylamine <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 n/a

Nitrobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 n/a

Parameter Threshold

SVOCS (mg/kg)

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 15 רשות ניקוז נחלים קישון

TM: 6.09 טבלה

יוצגו בדו"חות SP222 -ו SP213 ,SP214 ,SP215 ,SP216 ,SP217 ,SP219לבאצ' TMתוצאות עבור

.Jones UK –הבאים, כאשר התוצאות ייתקבלו מ

תשטיפים – Leachable Metals:6.10 טבלה

יוצגו SP222 -ו SP213 ,SP214 ,SP215 ,SP216 ,SP217 ,SP219לבאצ' תוצאות עבור תשטיפים

.Jones UK –בדו"חות הבאים, כאשר התוצאות ייתקבלו מ

L4סיכום

.חריגות ונרשמלא ו"חבמהלך תקופת הד

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 16 רשות ניקוז נחלים קישון

7.0 L5 – לאחר ערבוב במהלך ביורמידיאציה סדימנט

פיילוט מהוא חלק SP166 באצ'ה .SP166עבור באצ'ים L5במהלך תקופת הדו"ח נאספו שתי דוגמאות

שורות טיפול 2 –פוצל ל הבאצ'לגזם. חלופה אפשריתפטריות כאמה של קומפוסט של בדיקת הת

אחת מהשורות פוצלה באמצע, כל .טרי V3ה תוספת של קיבל מבין השתיים כאשר שורה אחת

.קיבלה תוספת גזם והמחצית השנייה תוספת קומפוסט פטריותכאשר מחצית מהשורה

. אחת טיפול שורת רק נותרה בפיילוט כן ועל אישור עברה V3 תוספת שקיבלה ההשור

(SP166 לוט) מפורט TPH: 7.01 טבלה

(SP166 לוט)כללי TPH: 7.02 טבלה

(SP166 לוט) תכולת לחות: 7.03טבלה

L5סיכום

.8/10/2015בתאריך TPHבמהלך תקופת הדו"ח נרשמה חריגה אחת בערכי

Sample IDLot/

BatchDescription

Sampled

Date>C5-C6 >C6-C8 >C8-C10

>C10-

C12

>C12-

C16

>C16-

C21

>C21-

C35 >C35-C44 Total

K3784 SP166 Soil 10/08/2015 <0.1 <0.1 <0.1 <0.2 67 275 609 108 1059

K3785 SP166 Soil 10/08/2015 <0.1 <0.1 <0.1 <0.2 68 327 636 107 1138

Aliphatics (mg/kg)

Sample IDLot/

BatchDescription

Sampled

Date

>EC5-

EC7

>EC7-

EC8

>EC8-

EC10

>EC10-

EC12

>EC12-

EC16

>EC16-

EC21

>EC21-

EC35

>EC35-

EC44Total

K3784 SP166 Soil 10/08/2015 <0.1 <0.1 <0.1 <0.2 13 103 421 56 593

K3785 SP166 Soil 10/08/2015 <0.1 <0.1 <0.1 <0.2 8 112 411 58 589

Aromatics (mg/kg)

Sample ID Lot/ Batch DescriptionSampled

Date

Total aliphatics

and aromatics

(C5-44)

Threshold

K3784 SP166 Soil 10/08/2015 1652 1560

K3785 SP166 Soil 10/08/2015 1727 1560

TOTAL TPH (mg/kg)

K3784 K3785

SP166 SP166

Soil Soil

10/08/2015 10/08/2015

Moisture

Content21.3 22.5

Parameter

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 17 רשות ניקוז נחלים קישון

0.0 L6 – נט מעורבב לאחר ביורמידיאציהסדימ

.L6במהלך תקופת הדו"ח לא נאספו דוגמאות

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 18 רשות ניקוז נחלים קישון

ולידציה סופית 0.0

, SP209 תוצאות ולידציה סופית התקבלו במהלך תקופת דו"ח זה עבור הבאצ'ים שחמ

SP225,SP226,SP227 ו- SP228.

(SP228 -ו SP209 ,SP225,SP226,SP227 )לוטים סופית ולידציה: 9.01 טבלה

Sample ID Lot/ Batch Description

Final

Validation

Location

Sampled

Date

Total aliphatics and

aromatics(C5-44)

Total TPH

average Threshold

K3782 S226 Cake L4 06/10/2015 572 - 1560

K3783 S227 Cake L4 06/10/2015 905 - 1560

K3786 S228 Cake L4 11/10/2015 1557 - 1560

K3787 SP225 Soil L4 12/10/2015 71 - 1560

K3788-1 SP209 Soil L4 13/10/2015 506 1560

K3788-2 SP209 Soil L4 13/10/2015 429 1560

TOTAL TPH mg/kg

468

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 19 רשות ניקוז נחלים קישון

10.0 V7 - ניטור איכות אויר חודשי

לאחר תוצאות יוצגו ה-Jones UK, הדוגמאות נשלחו ל, V7התבצע דיגום במהלך תקופת דו"ח זה

.Jones UK –ן מ קבלת

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 20 רשות ניקוז נחלים קישון

מאורעות ניטור חריגים 11.0

אין מאורעות חריגים לדווח.

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 21 רשות ניקוז נחלים קישון

מפרט האתר – 1נספח

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 22 רשות ניקוז נחלים קישון

: סכמת ולידציה1איור

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 23 רשות ניקוז נחלים קישון

: מפרט האתר הראשי2איור

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 24 רשות ניקוז נחלים קישון

L4 -ו L3: מיקום 3איור

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 25 רשות ניקוז נחלים קישון

(Windrows: מיקום שורות הטיפול )4איור

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פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי

18/10/2015 26 רשות ניקוז נחלים קישון

JONES ENVIRONMENTAL LABORATORYדו"חות ולידציה ממעבדת – 2נפסח

Page 30: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

Unit 3 Deeside Point

Zone 3

Deeside Industrial Park

Deeside

Englobe Corp

Attention :

Date :

Your reference :

Our reference :

Location :

Date samples received :

Status :

Issue :

Dave Adams

Ha'Ashlag 27

Haifa

Israel

Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK

Jones Environmental Laboratory

CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

Three samples were received for analysis on 19th August, 2015 of which one were scheduled for analysis. Please find attached our Test Report

which should be read with notes at the end of the report and should include all sections if reproduced. Interpretations and opinions are outside the

scope of any accreditation, and all results relate only to samples supplied.

All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.

Simon Gomery BSc

Project Manager

4th September, 2015

Kishon

Kishon

19th August, 2015

Final report

Compiled By:

Test Report 15/11590 Batch 1 Schedule B 15/11590 Batch 1 Schedule C

1

QF-PM 3.1.1 v16Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 4

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Client Name: Report : Solid

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/11590

J E Sample No. 3-4

Sample ID K3562

Depth

COC No / misc VS-081315-L3-1

Containers V J

Sample Date <>

Sample Type Soil

Batch Number 1

Date of Receipt 19/08/2015

Aluminium 57170AA <50 mg/kg TM30/PM15

Antimony <1 <1 mg/kg TM30/PM15

Arsenic # 43.0 <0.5 mg/kg TM30/PM15

Beryllium 2.1 <0.5 mg/kg TM30/PM15

Cadmium # 13.2 <0.1 mg/kg TM30/PM15

Chromium # 138.0 <0.5 mg/kg TM30/PM15

Cobalt # 16.5 <0.5 mg/kg TM30/PM15

Copper # 128 <1 mg/kg TM30/PM15

Iron 47310 <20 mg/kg TM30/PM15

Lead # 36 <5 mg/kg TM30/PM15

Manganese # 614 <1 mg/kg TM30/PM15

Nickel # 56.0 <0.7 mg/kg TM30/PM15

Selenium # 1 <1 mg/kg TM30/PM15

Thallium <1 <1 mg/kg TM30/PM15

Titanium 1400 <5 mg/kg TM30/PM15

Vanadium 129 <1 mg/kg TM30/PM15

Water Soluble Boron # 27.3 <0.1 mg/kg TM74/PM32

Zinc # 443 <5 mg/kg TM30/PM15

Mercury CVAF <0.5 <0.5 mg/kg TM61/PM62

Hexavalent Chromium # <0.3 <0.3 mg/kg TM38/PM20

Jones Environmental Laboratory

Englobe Corp

Kishon

Kishon

Dave Adams

Please see attached notes for all

abbreviations and acronyms

LOD/LOR UnitsMethod

No.

QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 4

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JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

NOTE

JE Job No.:

#

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

AA

Trip Blank Sample

AQC Sample

Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable

containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and

any test results that may be compromised highlighted on your deviating samples report.

MCERTS accredited.

ISO17025 (UKAS) accredited - UK.

15/11590

AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

Please note we are not a UK Drinking Water Inspectorate (DWI) Approved Laboratory .

ISO17025 (UKAS) accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are

outside our scope of accreditation.

Blank Sample

Client Sample

Analysis subcontracted to a Jones Environmental approved laboratory.

Calibrated against a single substance

Not applicable

Suspected carry over

ABBREVIATIONS and ACRONYMS USED

Samples are dried at 35°C ±5°C

Indicates analyte found in associated method blank.

No Asbestos Detected.

No Determination Possible

NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS

Please note we are only MCERTS accredited (UK soils only) for sand, loam and clay and any other matrix is outside our scope of accreditation.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

15/11590

WATERS

Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our

MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations

of them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS

accredited.

Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.

It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be

included unless we are requested to remove them.

If you have not already done so, please send us a purchase order if this is required by your company.

% Asbestos in Asbestos Containing Materials (ACMs) is determined by reference to HSG 264 The Survey Guide - Appendix 2 : ACMs in buildings

listed in order of ease of fibre release.

All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless

otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.

x5 Dilution

Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.

All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary.

Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to

peat, clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids.

Acceptable limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance

criteria but the associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.

A dilution suffix indicates a dilution has been performed and the reported result takes this into account. No further calculation is required.

Outside Calibration Range

No Fibres Detected

Result outside calibration range, results should be considered as indicative only and are not accredited.

Results expressed on as received basis.

Surrogate recovery outside performance criteria. This may be due to a matrix effect.

Data is only reported if the laboratory is confident that the data is a true reflection of the samples analysed. Data is only reported as accredited

when all the requirements of our Quality System have been met. In certain circumstances where all the requirements of the Quality System have

not been met, for instance if the associated AQC has failed, the reason is fully investigated and documented. The sample data is then evaluated

alongside the other quality control checks performed during analysis to determine its suitability. Following this evaluation, provided the sample

results have not been effected, the data is reported but accreditation is removed. It is a UKAS requirement for data not reported as accredited to

be considered indicative only, but this does not mean the data is not valid.

Where possible, and if requested, samples will be re-extracted and a revised report issued with accredited results. Please do not hesitate to

contact the laboratory if further details are required of the circumstances which have led to the removal of accreditation.

Matrix Effect

As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting

samples.

None Detected (usually refers to VOC and/SVOC TICs).

Limit of Detection (Limit of Reporting) in line with ISO 17025 and MCERTS

Dilution required.

QF-PM 3.1.9 v31Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 4

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JE Job No: 15/11590

Test Method No. Description

Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -

Optical Emission Spectrometry). Modified US EPA Method 200.7PM15

Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5

°C. Samples containing asbestos are not dried and ground.AD Yes

TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -

Optical Emission Spectrometry). Modified US EPA Method 200.7PM15

Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5

°C. Samples containing asbestos are not dried and ground.Yes AD Yes

TM38Soluble Ion analysis using the Thermo Aquakem Photometric Automatic Analyser.

Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM20

Extraction of dried and ground samples with deionised water in a 2:1 water to solid

ratio for anions. Extraction of as received samples with deionised water in a 2:1 water

to solid ratio for ammoniacal nitrogen. Samples are extracted using an orbital shaker.

Yes AR Yes

TM61Modified US EPA methods 245.7 and 200.7. Determination of Mercury by Cold Vapour

Atomic Fluorescence. PM62 Acid digestion of as received solid samples using Aqua Regia refluxed at 112.5 °C. AR Yes

TM74 Analysis of water soluble boron (20:1 extract) by ICP-OES. PM32 Hot water soluble boron is extracted from dried and ground samples using a 20:1 ratio. Yes AD Yes

Jones Environmental Laboratory Method Code Appendix

QF-PM 3.1.10 v14 Please include all sections of this report if it is reproduced 4 of 4

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Unit 3 Deeside Point

Zone 3

Deeside Industrial Park

Deeside

A.D. Edan Hadash

Attention :

Date :

Your reference :

Our reference :

Location :

Date samples received :

Status :

Issue :

Dave Adams

Kishon Project

Ha'Ashlag 30

Haifa

3295163

Israel

Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK

Jones Environmental Laboratory

CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

Eighteen samples were received for analysis on 9th October, 2015 of which eighteen were scheduled for analysis. Please find attached our Test

Report which should be read with notes at the end of the report and should include all sections if reproduced. Interpretations and opinions are

outside the scope of any accreditation, and all results relate only to samples supplied.

All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.

Simon Gomery BSc

Project Manager

14th October, 2015

Kishon

9th October, 2015

Final report

Compiled By:

Test Report 15/14490 Batch 1

1

QF-PM 3.1.1 v16Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 10

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Client Name: Report : Solid

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/14490

J E Sample No. 1 2 3 4 5 6 7 8 9 10

Sample ID K3717 K3718 K3729-1 K3729-2 K3730-1 K3730-2 K3731-1 K3731-2 K3732-1 K3732-2

Depth

COC No / misc VS-092015-L3-1 VS-092015-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092415-L4-1 VS-092415-L4-1

Containers B B B B B B B B B B

Sample Date 20/09/2015 20/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 24/09/2015 24/09/2015

Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil

Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015

Aluminium 47830 37280 35510 37090 42760 41960 46380 44240 47790 42810 <50 mg/kg TM30/PM15

Antimony <1 <1 <1 1 1 1 1 2 1 <1 <1 mg/kg TM30/PM15

Arsenic # 31.4 26.4 6.2 5.3 7.1 6.0 13.6 10.6 14.9 8.6 <0.5 mg/kg TM30/PM15

Beryllium 1.7 1.4 1.3 1.4 1.7 1.6 1.7 1.8 1.9 1.6 <0.5 mg/kg TM30/PM15

Cadmium # 14.7 8.1 2.6 2.4 3.8 1.7 15.6 14.8 11.9 6.8 <0.1 mg/kg TM30/PM15

Chromium # 119.6 100.9 67.2 72.7 84.0 75.5 120.9 122.2 117.7 92.6 <0.5 mg/kg TM30/PM15

Cobalt # 13.9 11.3 16.1 16.4 18.5 19.6 16.4 17.2 17.9 16.6 <0.5 mg/kg TM30/PM15

Copper # 120 80 41 39 44 34 127 119 102 63 <1 mg/kg TM30/PM15

Iron 38950 30740 33080 34570 40520 40100 37960 38610 42760 37990 <20 mg/kg TM30/PM15

Lead # 28 24 8 7 9 7 21 29 20 13 <5 mg/kg TM30/PM15

Manganese # 330 301 650 594 722 696 528 592 595 623 <1 mg/kg TM30/PM15

Nickel # 51.7 40.7 42.9 45.0 51.6 51.9 54.7 53.8 56.0 48.6 <0.7 mg/kg TM30/PM15

Selenium # <1 <1 <1 <1 <1 <1 <1 1 <1 <1 <1 mg/kg TM30/PM15

Thallium <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 mg/kg TM30/PM15

Titanium 1268 988 1077 1194 1128 1333 1329 1121 1202 1231 <5 mg/kg TM30/PM15

Vanadium 114 85 74 77 91 87 126 124 122 94 <1 mg/kg TM30/PM15

Water Soluble Boron # 21.6 16.4 6.3 4.9 6.1 6.8 8.7 4.4 5.1 10.2 <0.1 mg/kg TM74/PM32

Zinc # 460 294 122 123 153 116 463 420 349 224 <5 mg/kg TM30/PM15

Mercury CVAF <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 mg/kg TM61/PM62

Natural Moisture Content 210.1 75.2 20.7 17.6 21.8 23.6 33.3 33.5 28.6 20.9 <0.1 % PM4/PM0

Hexavalent Chromium # <0.3 0.7 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 mg/kg TM38/PM20

Please see attached notes for all

abbreviations and acronyms

LOD/LOR UnitsMethod

No.

Jones Environmental Laboratory

A.D. Edan Hadash

Kishon

Dave Adams

QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 10

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Client Name: Report : Solid

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/14490

J E Sample No. 11 12 13 14 15 16 17 18

Sample ID K3733 K3734-1 K3734-2 K3735-1 K3735-2 K3736-1 K3736-2 K3752

Depth

COC No / misc VS-092415-L4-1 VS-092415-L4-1 VS-092415-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-093015-L3-1

Containers B B B B B B B B

Sample Date 24/09/2015 24/09/2015 24/09/2015 29/09/2015 29/09/2015 29/09/2015 29/09/2015 30/09/2015

Sample Type Soil Soil Soil Soil Soil Soil Soil Soil

Batch Number 1 1 1 1 1 1 1 1

Date of Receipt 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015

Aluminium 32700 43960 47110 36640 34670 40210 38030 40850 <50 mg/kg TM30/PM15

Antimony 1 <1 <1 <1 <1 <1 <1 <1 <1 mg/kg TM30/PM15

Arsenic # 10.6 19.0 11.7 12.3 12.6 18.9 21.0 26.4 <0.5 mg/kg TM30/PM15

Beryllium 1.2 1.6 1.7 1.4 1.4 1.5 1.5 1.4 <0.5 mg/kg TM30/PM15

Cadmium # 5.7 7.0 5.9 7.3 7.9 8.1 8.2 9.1 <0.1 mg/kg TM30/PM15

Chromium # 73.3 93.2 91.1 86.9 94.4 96.6 99.9 95.2 <0.5 mg/kg TM30/PM15

Cobalt # 12.9 15.4 18.0 14.2 12.9 13.5 13.2 12.4 <0.5 mg/kg TM30/PM15

Copper # 55 76 60 71 77 79 84 89 <1 mg/kg TM30/PM15

Iron 28960 36510 40380 31910 29870 33470 33320 33250 <20 mg/kg TM30/PM15

Lead # 12 17 11 16 19 19 22 23 <5 mg/kg TM30/PM15

Manganese # 430 484 604 451 423 401 429 319 <1 mg/kg TM30/PM15

Nickel # 37.7 47.8 52.9 42.5 41.0 44.1 42.1 43.6 <0.7 mg/kg TM30/PM15

Selenium # <1 <1 <1 <1 <1 <1 <1 <1 <1 mg/kg TM30/PM15

Thallium <1 <1 <1 <1 <1 <1 <1 <1 <1 mg/kg TM30/PM15

Titanium 953 1277 1347 1111 915 1182 1008 1110 <5 mg/kg TM30/PM15

Vanadium 75 95 99 87 88 92 92 93 <1 mg/kg TM30/PM15

Water Soluble Boron # 8.8 14.1 12.0 9.6 10.5 11.6 15.4 19.9 <0.1 mg/kg TM74/PM32

Zinc # 197 269 214 250 276 280 294 323 <5 mg/kg TM30/PM15

Mercury CVAF <0.5 <0.5 <0.5 0.7 <0.5 <0.5 <0.5 <0.5 <0.5 mg/kg TM61/PM62

Natural Moisture Content 25.9 38.2 32.7 35.0 34.7 49.0 46.5 151.6 <0.1 % PM4/PM0

Hexavalent Chromium # <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 mg/kg TM38/PM20

LOD/LOR UnitsMethod

No.

Jones Environmental Laboratory

A.D. Edan Hadash

Kishon

Dave Adams

Please see attached notes for all

abbreviations and acronyms

QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 10

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Client Name: Report : CEN 10:1 1 Batch

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/14490

J E Sample No. 2 3 4 5 6 7 8 9 10 11

Sample ID K3718 K3729-1 K3729-2 K3730-1 K3730-2 K3731-1 K3731-2 K3732-1 K3732-2 K3733

Depth

COC No / misc VS-092015-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092415-L4-1 VS-092415-L4-1 VS-092415-L4-1

Containers B B B B B B B B B B

Sample Date 20/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 24/09/2015 24/09/2015 24/09/2015

Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil

Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015

Dissolved Antimony # <0.002 0.002 <0.002 0.003 0.002 0.003 0.004 0.003 0.003 <0.002 <0.002 mg/l TM30/PM17

Dissolved Arsenic # 0.0159 0.0029 <0.0025 <0.0025 <0.0025 <0.0025 <0.0025 0.0031 <0.0025 <0.0025 <0.0025 mg/l TM30/PM17

Dissolved Beryllium # <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 mg/l TM30/PM17

Dissolved Cadmium # <0.0005 <0.0005 0.0007 <0.0005 0.0009 0.0034 0.0045 0.0012 0.0025 0.0010 <0.0005 mg/l TM30/PM17

Dissolved Chromium # <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 mg/l TM30/PM17

Dissolved Cobalt # <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 mg/l TM30/PM17

Dissolved Copper # <0.007 0.013 0.018 0.012 0.012 0.024 0.031 0.011 0.019 0.013 <0.007 mg/l TM30/PM17

Dissolved Lead # <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 mg/l TM30/PM17

Dissolved Manganese # 0.163 0.007 0.008 0.099 0.045 0.091 0.086 0.148 0.042 0.075 <0.002 mg/l TM30/PM17

Dissolved Nickel # 0.015 0.004 0.005 0.006 0.005 0.009 0.012 0.007 0.007 0.006 <0.002 mg/l TM30/PM17

Dissolved Selenium # <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 mg/l TM30/PM17

Dissolved Thallium # <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 mg/l TM30/PM17

Dissolved Vanadium # 0.0094 0.0160 0.0182 0.0165 0.0129 0.0312 0.0352 0.0244 0.0244 0.0153 <0.0015 mg/l TM30/PM17

Dissolved Zinc # 0.004 0.007 0.009 0.008 0.007 0.022 0.028 0.019 0.015 0.010 <0.003 mg/l TM30/PM17

Mercury Dissolved by CVAF # 0.00007 0.00004 0.00008 0.00002 0.00003 0.00008 0.00011 0.00008 0.00006 0.00004 <0.00001 mg/l TM61/PM38

Mass of raw test portion 0.167 0.1091 0.1112 0.1168 0.1177 0.1249 0.1273 0.1173 0.1144 0.119 kg NONE/PM17

Leachant Volume 0.823 0.881 0.879 0.873 0.872 0.866 0.862 0.872 0.875 0.871 l NONE/PM17

Hexavalent Chromium <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 mg/l TM38/PM0

Please see attached notes for all

abbreviations and acronyms

LOD/LOR UnitsMethod

No.

Jones Environmental Laboratory

A.D. Edan Hadash

Kishon

Dave Adams

QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 4 of 10

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Client Name: Report : CEN 10:1 1 Batch

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/14490

J E Sample No. 12 13 14 15 16 17

Sample ID K3734-1 K3734-2 K3735-1 K3735-2 K3736-1 K3736-2

Depth

COC No / misc VS-092415-L4-1 VS-092415-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-092915-L4-1

Containers B B B B B B

Sample Date 24/09/2015 24/09/2015 29/09/2015 29/09/2015 29/09/2015 29/09/2015

Sample Type Soil Soil Soil Soil Soil Soil

Batch Number 1 1 1 1 1 1

Date of Receipt 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015

Dissolved Antimony # <0.002 <0.002 0.003 <0.002 <0.002 0.002 <0.002 mg/l TM30/PM17

Dissolved Arsenic # <0.0025 <0.0025 0.0028 0.0033 0.0052 <0.0025 <0.0025 mg/l TM30/PM17

Dissolved Beryllium # <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 mg/l TM30/PM17

Dissolved Cadmium # 0.0006 0.0007 <0.0005 0.0009 0.0005 <0.0005 <0.0005 mg/l TM30/PM17

Dissolved Chromium # <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 mg/l TM30/PM17

Dissolved Cobalt # <0.002 <0.002 <0.002 <0.002 0.003 0.002 <0.002 mg/l TM30/PM17

Dissolved Copper # 0.009 0.008 <0.007 0.008 <0.007 <0.007 <0.007 mg/l TM30/PM17

Dissolved Lead # <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 mg/l TM30/PM17

Dissolved Manganese # 0.032 0.074 0.436 0.231 0.914 0.587 <0.002 mg/l TM30/PM17

Dissolved Nickel # 0.005 0.004 0.009 0.008 0.009 0.008 <0.002 mg/l TM30/PM17

Dissolved Selenium # <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 mg/l TM30/PM17

Dissolved Thallium # <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 mg/l TM30/PM17

Dissolved Vanadium # 0.0147 0.0128 0.0188 0.0195 0.0105 0.0128 <0.0015 mg/l TM30/PM17

Dissolved Zinc # 0.009 0.007 0.010 0.014 <0.003 0.006 <0.003 mg/l TM30/PM17

Mercury Dissolved by CVAF # 0.00003 0.00001 0.00007 0.00008 0.00005 0.00009 <0.00001 mg/l TM61/PM38

Mass of raw test portion 0.1241 0.1188 0.1271 0.1221 0.145 0.1338 kg NONE/PM17

Leachant Volume 0.866 0.871 0.863 0.868 0.845 0.857 l NONE/PM17

Hexavalent Chromium <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 mg/l TM38/PM0

LOD/LOR UnitsMethod

No.

Jones Environmental Laboratory

A.D. Edan Hadash

Kishon

Dave Adams

Please see attached notes for all

abbreviations and acronyms

QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 5 of 10

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Notification of Deviating Samples

J E

Job

No.

Batch Depth J E Sample

No.Analysis Reason

Please note that only samples that are deviating are mentioned in this report. If no samples are listed it is because none were deviating.

Only analyses which are accredited are recorded as deviating if set criteria are not met.

Jones Environmental Laboratory

Kishon

Dave AdamsContact:

Sample ID

Client Name: A.D. Edan Hadash

Reference:

Location:

No deviating sample report results for job 15/14490

QF-PM 3.1.11 v3 Please include all sections of this report if it is reproduced 6 of 10

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JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

NOTE

Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to

peat, clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids.

Acceptable limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance

criteria but the associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.

A dilution suffix indicates a dilution has been performed and the reported result takes this into account. No further calculation is required.

Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.

ISO17025 (UKAS) accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are

outside our scope of accreditation.

As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting

samples.

% Asbestos in Asbestos Containing Materials (ACMs) is determined by reference to HSG 264 The Survey Guide - Appendix 2 : ACMs in buildings

listed in order of ease of fibre release.

All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C

unless otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

Please note we are not a UK Drinking Water Inspectorate (DWI) Approved Laboratory .

Negative Neutralization Potential (NP) values are obtained when the volume of NaOH (0.1N) titrated (pH 8.3) is greater than the volume of HCl

(1N) to reduce the pH of the sample to 2.0 - 2.5. Any negative NP values are corrected to 0.

Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.

Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable

containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed

and any test results that may be compromised highlighted on your deviating samples report.

NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS

Please note we are only MCERTS accredited (UK soils only) for sand, loam and clay and any other matrix is outside our scope of accreditation.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

15/14490

WATERS

Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our

MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations

of them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS

accredited.

It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be

included unless we are requested to remove them.

All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary.

If you have not already done so, please send us a purchase order if this is required by your company.

QF-PM 3.1.9 v32Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 7 of 11

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Data is only reported if the laboratory is confident that the data is a true reflection of the samples analysed. Data is only reported as accredited

when all the requirements of our Quality System have been met. In certain circumstances where all the requirements of the Quality System have

not been met, for instance if the associated AQC has failed, the reason is fully investigated and documented. The sample data is then evaluated

alongside the other quality control checks performed during analysis to determine its suitability. Following this evaluation, provided the sample

results have not been effected, the data is reported but accreditation is removed. It is a UKAS requirement for data not reported as accredited to

be considered indicative only, but this does not mean the data is not valid.

Where possible, and if requested, samples will be re-extracted and a revised report issued with accredited results. Please do not hesitate to

contact the laboratory if further details are required of the circumstances which have led to the removal of accreditation.

QF-PM 3.1.9 v32Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 8 of 11

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JE Job No.:

#

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

MCERTS accredited.

ISO17025 (UKAS) accredited - UK.

15/14490

AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.

Calibrated against a single substance

Not applicable

No Asbestos Detected.

No Determination Possible

Indicates analyte found in associated method blank.

None Detected (usually refers to VOC and/SVOC TICs).

Outside Calibration Range

No Fibres Detected

Result outside calibration range, results should be considered as indicative only and are not accredited.

Results expressed on as received basis.

Surrogate recovery outside performance criteria. This may be due to a matrix effect.

Limit of Detection (Limit of Reporting) in line with ISO 17025 and MCERTS

Analysis subcontracted to a Jones Environmental approved laboratory.

Matrix Effect

Blank Sample

Client Sample

Trip Blank Sample

AQC Sample

Suspected carry over

ABBREVIATIONS and ACRONYMS USED

Samples are dried at 35°C ±5°C

Dilution required.

QF-PM 3.1.9 v32Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 9 of 11

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JE Job No: 15/14490

Test Method No. Description

Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

PM4Gravimetric measurement of Natural Moisture Content and % Moisture Content at

either 35°C or 105°C. Calculation based on ISO 11465 and BS1377.PM0 No preparation is required.

TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -

Optical Emission Spectrometry). Modified US EPA Method 200.7PM15

Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5

°C. Samples containing asbestos are not dried and ground.AD Yes

TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -

Optical Emission Spectrometry). Modified US EPA Method 200.7PM15

Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5

°C. Samples containing asbestos are not dried and ground.Yes AD Yes

TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -

Optical Emission Spectrometry). Modified US EPA Method 200.7PM17

Modified method EN12457-2 As received solid samples are leached with water in a

10:1 water to soil ratio for 24 hours, the moisture content of the sample is included in

the ratio.

Yes AR Yes

TM38Soluble Ion analysis using the Thermo Aquakem Photometric Automatic Analyser.

Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM0 No preparation is required. AR Yes

TM38Soluble Ion analysis using the Thermo Aquakem Photometric Automatic Analyser.

Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM20

Extraction of dried and ground samples with deionised water in a 2:1 water to solid

ratio for anions. Extraction of as received samples with deionised water in a 2:1 water

to solid ratio for ammoniacal nitrogen. Samples are extracted using an orbital shaker.

Yes AR Yes

TM61Modified US EPA methods 245.7 and 200.7. Determination of Mercury by Cold Vapour

Atomic Fluorescence. PM38

Samples are brominated to reduce all mercury compounds to Mercury (II) which is

analysed using method TM061.Yes AR Yes

TM61Modified US EPA methods 245.7 and 200.7. Determination of Mercury by Cold Vapour

Atomic Fluorescence. PM62 Acid digestion of as received solid samples using Aqua Regia refluxed at 112.5 °C. AR Yes

TM74 Analysis of water soluble boron (20:1 extract) by ICP-OES. PM32 Hot water soluble boron is extracted from dried and ground samples using a 20:1 ratio. Yes AD Yes

NONE No Method Code PM17

Modified method EN12457-2 As received solid samples are leached with water in a

10:1 water to soil ratio for 24 hours, the moisture content of the sample is included in

the ratio.

Jones Environmental Laboratory Method Code Appendix

QF-PM 3.1.10 v14 Please include all sections of this report if it is reproduced 10 of 10

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Client Name: Report : Solid

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/688

J E Sample No. 1 4 5 6 7 10 13

Sample ID K3753 K3754 K3755 K3780 K3782 K3783 K3781

Depth

COC No / misc VS-093015-L4-1 VS-093015-L5-PT1-2 VS-093015-L5-PT2-2 VS-100115-L3-1 VS-100615-L4-1 VS-100615-L4-1 VS-100415-L3-1

Containers T T T T T T T

Sample Date 30/09/2015 30/09/2015 30/09/2015 01/10/2015 06/10/2015 06/10/2015 06/10/2015

Sample Type Solid Solid Solid Solid Solid Solid Solid

Batch Number 1 1 1 1 1 1 1

Date of Receipt 06/10/2015 06/10/2015 06/10/2015 06/10/2015 06/10/2015 06/10/2015 06/10/2015

TPH CWG

Aliphatics

>C5-C6 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>C6-C8 0.2 <0.1 <0.1 1.2 0.2 0.6 0.6 <0.1 mg/kg TM36/PM12

>C8-C10 2.2 <0.1 <0.1 5.7 2.6 4.5 5.6 <0.1 mg/kg TM36/PM12

>C10-C12 31.3 <0.2 <0.2 232.8 25.4 48.0 197.9 <0.2 mg/kg TM5/PM16

>C12-C16 102 76 72 756 93 164 570 <4 mg/kg TM5/PM16

>C16-C21 77 258 361 567 75 120 446 <7 mg/kg TM5/PM16

>C21-C35 160 576 756 1401 163 280 1087 <7 mg/kg TM5/PM16

>C35-C44 13 82 103 165 31 26 178 <7 mg/kg TM5/PM16

Total aliphatics C5-44 386 992 1292 3129 390 643 2485 <26 mg/kg TM5/TM36/PM16

Aromatics

>C5-EC7 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>EC7-EC8 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>EC8-EC10 0.2 <0.1 <0.1 0.9 0.2 0.4 0.6 <0.1 mg/kg TM36/PM12

>EC10-EC12 <0.2 <0.2 <0.2 <0.2 <0.2 48.0 <0.2 <0.2 mg/kg TM5/PM16

>EC12-EC16 42 12 <4 141 21 164 33 <4 mg/kg TM5/PM16

>EC16-EC21 55 109 121 267 46 120 137 <7 mg/kg TM5/PM16

>EC21-EC35 179 430 497 1095 115 280 564 <7 mg/kg TM5/PM16

>EC35-EC44 20 86 95 162 <7 26 77 <7 mg/kg TM5/PM16

Total aromatics C5-44 296 637 713 1666 182 638 812 <26 mg/kg TM5/TM36/PM16

Total aliphatics and aromatics(C5-44) 682 1629 2005 4795 572 1281 3297 <52 mg/kg TM5/TM36/PM16

Natural Moisture Content 82.2 22.8 20.6 200.0 71.3 102.7 197.1 <0.1 % PM4/PM0

Moisture Content 45.1 18.6 17.1 66.7 41.6 50.7 66.3 <0.1 % PM4/PM0

pH 7.14 - - - 7.22 7.12 - <0.01 pH units TM19/PM11

Please see attached notes for all

abbreviations and acronyms

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

QF-PM 3.1.2 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 1

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Ha’Ashlag 27

Haifa

Israel

3295163

Kishon Project

Attention :

Date :

Your reference :

Our reference :

Location :

Date samples received :

Status :

Issue :

David Adams

Haifa

Israel

Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK

Jones Environmental Laboratory

Tel: +972 58 401 0455

Two samples were received for analysis on 8th October, 2015. Please find attached our Test Report which should be read with notes at the end of

the report and should include all sections if reproduced. Interpretations and opinions are outside the scope of any accreditation, and all results relate

only to samples supplied.

All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.

Dave Adams

Site Scientist

12th October, 2015

8th October, 2015

Final report

Compiled By:

Test Report 15/689 Batch 1

1

QF-PM 3.1.1 v15Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 4

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Client Name: Report : Solid

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/689

J E Sample No. 1 2

Sample ID K3784 K3785

Depth

COC No / misc VS-100815-L5-PT1-3 VS-100815-L5-PT2-3

Containers T T

Sample Date 08/10/2015 08/10/2015

Sample Type Solid Solid

Batch Number 1 1

Date of Receipt 08/10/2015 08/10/2015

TPH CWG

Aliphatics

>C5-C6 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>C6-C8 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>C8-C10 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>C10-C12 <0.2 <0.2 <0.2 mg/kg TM5/PM16

>C12-C16 67 68 <4 mg/kg TM5/PM16

>C16-C21 275 327 <7 mg/kg TM5/PM16

>C21-C35 609 636 <7 mg/kg TM5/PM16

>C35-C44 108 107 <7 mg/kg TM5/PM16

Total aliphatics C5-44 1059 1138 <26 mg/kg TM5/TM36/PM16

Aromatics

>C5-EC7 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>EC7-EC8 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>EC8-EC10 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>EC10-EC12 <0.2 <0.2 <0.2 mg/kg TM5/PM16

>EC12-EC16 13 8 <4 mg/kg TM5/PM16

>EC16-EC21 103 112 <7 mg/kg TM5/PM16

>EC21-EC35 421 411 <7 mg/kg TM5/PM16

>EC35-EC44 56 58 <7 mg/kg TM5/PM16

Total aromatics C5-44 593 589 <26 mg/kg TM5/TM36/PM16

Total aliphatics and aromatics(C5-44) 1652 1727 <52 mg/kg TM5/TM36/PM16

Natural Moisture Content 27.1 29.1 <0.1 % PM4/PM0

Moisture Content 21.3 22.5 <0.1 % PM4/PM0

Please see attached notes for all

abbreviations and acronyms

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

QF-PM 3.1.2 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 4

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JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

NOTE

JE Job No.:

#

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

CO

OC

NFD

Calibrated against a single substance.

No Determination Possible

ABBREVIATIONS and ACRONYMS USED

No Asbestos Detected.

None Detected (usually refers to VOC and/SVOC TICs).

UKAS accredited.

If you have not already done so, please send us a purchase order if this is required by your company.

All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless

otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.

No Fibres Detected

Result outside calibration range, results should be considered as indicative only and are not accredited.

Results expressed on as received basis.

Surrogate recovery outside performance criteria. This may be due to a matrix effect.

Data is only accredited when all the requirements of our Quality System have been met. In certain circumstances where the requirements have not

been met, the laboratory may issue the data in an interim report but will remove the accreditation, in this instance results should be considered

indicative only. Where possible samples will be re-extracted and a final report issued with accredited results. Please do not hesitate to contact the

laboratory if further details are required of the circumstances which have led to the removal of accreditation.

Dilution required.

Indicates analyte found in associated method blank.

Not applicable

MCERTS accredited.

AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.

Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to peat,

clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids. Acceptable

limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance criteria but the

associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.

Analysis subcontracted to a Jones Environmental approved laboratory.

Outside Calibration Range

Suspected carry over

NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS

Please note we are only MCERTS accredited for sand, loam and clay and any other matrix is outside our scope of accreditation.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

15/689

WATERS

15/689

Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our

MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations of

them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS

accredited.

All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary. If we are instructed to keep samples, a

storage charge of £1 (1.5 Euros) per sample per month will be applied until we are asked to dispose of them.

It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be

included unless we are requested to remove them.

UKAS accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are outside our

scope of accreditation

As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting samples.

Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable

containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and

any test results that may be compromised highlighted on your deviating samples report.

Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.

Please note we are not a Drinking Water Inspectorate (DWI) Approved Laboratory . It is important that detection limits are carefully considered when

requesting water analysis.

QF-PM 3.1.9 v25Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 4

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JE Job No: 15/689

Test Method No. Description

Prep Method

No. (if

appropriate)

Description UKAS

MCERTS

(soils

only)

Analysis done on

As Received

(AR) or Air Dried

(AD)

Reported on

dry weight

basis

PM4Gravimetric measurement of Natural Moisture Content and % Moisture Content at either

35°C or 105°C. Calculation based on ISO 11465 and BS1377.PM0 No preparation is required.

TM5

In-House method based on USEPA 8015B. Determination of Extractable Petroleum

Hydrocarbons (EPH) in the carbon chain length range of C8-40 by GC-FID. Accredited to

ISO 17025 on soil and water samples and MCERTS (carbon banding only) on soils. All

accreditation is matrix specific.

PM16 Aliphatic/Aromatic fractionation AR Yes

TM5/TM36 TPH CWG by GC-FID PM16 Aliphatic/Aromatic fractionation AR Yes

TM36

In-House method based on USEPA 8015B. Determination of Gasoline Range Organics

(GRO) in the carbon chain range of C5-12 by headspace GC-FID. Accredited to ISO

17025 on soil and water samples and MCERTS accredited (carbon banding only) on

soils. All accreditation is matrix specific.

PM12

In-house method based on USEPA 5021. Preparation of solid and liquid samples for

headspace analysis. Samples are spiked with surrogates to facilitate quantification. ISO

17025 accredited extraction method. All accreditation is matrix specific

AR Yes

Jones Environmental Laboratory Method Code Appendix

QF-PM 3.1.10 v13 Please include all sections of this report if it is reproduced 4 of 4

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Ha’Ashlag 27

Haifa

Israel

3295163

Kishon Project

Attention :

Date :

Your reference :

Our reference :

Location :

Date samples received :

Status :

Issue :

David Adams

Haifa

Israel

Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK

Jones Environmental Laboratory

Tel: +972 58 401 0455

One sample were received for analysis on 11th October, 2015. Please find attached our Test Report which should be read with notes at the end of

the report and should include all sections if reproduced. Interpretations and opinions are outside the scope of any accreditation, and all results relate

only to samples supplied.

All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.

Dave Adams

Site Scientist

12th October, 2015

11th October, 2015

Final report

Compiled By:

Test Report 15/691 Batch 1 Schedule A

1

QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 8

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QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 8

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Client Name: Report : Solid

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/691

J E Sample No. 1

Sample ID K3786

Depth

COC No / misc VS-101115-L4-1

Containers T

Sample Date 11/10/2015

Sample Type Solid

Batch Number 1

Date of Receipt 11/10/2015

TPH CWG

Aliphatics

>C5-C6 <0.1 <0.1 mg/kg TM36/PM12

>C6-C8 1.6 <0.1 mg/kg TM36/PM12

>C8-C10 2.9 <0.1 mg/kg TM36/PM12

>C10-C12 67.0 <0.2 mg/kg TM5/PM16

>C12-C16 183 <4 mg/kg TM5/PM16

>C16-C21 149 <7 mg/kg TM5/PM16

>C21-C35 507 <7 mg/kg TM5/PM16

>C35-C44 55 <7 mg/kg TM5/PM16

Total aliphatics C5-44 966 <26 mg/kg TM5/TM36/PM16

Aromatics

>C5-EC7 <0.1 <0.1 mg/kg TM36/PM12

>EC7-EC8 <0.1 <0.1 mg/kg TM36/PM12

>EC8-EC10 0.2 <0.1 mg/kg TM36/PM12

>EC10-EC12 <0.2 <0.2 mg/kg TM5/PM16

>EC12-EC16 39 <4 mg/kg TM5/PM16

>EC16-EC21 88 <7 mg/kg TM5/PM16

>EC21-EC35 403 <7 mg/kg TM5/PM16

>EC35-EC44 61 <7 mg/kg TM5/PM16

Total aromatics C5-44 591 <26 mg/kg TM5/TM36/PM16

Total aliphatics and aromatics(C5-44) 1557 <52 mg/kg TM5/TM36/PM16

Natural Moisture Content 96.5 <0.1 % PM4/PM0

Moisture Content 49.1 <0.1 % PM4/PM0

pH 7.38 <0.01 pH units TM19/PM11

Please see attached notes for all

abbreviations and acronyms

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 7

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Client Name: SVOC Report : Solid

Reference:

Location:

Contact:

JE Job No.: 15/691

J E Sample No. 1

Sample ID K3786

Depth

COC No / misc VS-101115-L4-1

Containers T

Sample Date 11/10/2015

Sample Type Solid

Batch Number 1

Date of Receipt 11/10/2015

SVOC MS

Phenols

2-Chlorophenol <0.01 <0.01 mg/kg TM16/PM8

2-Methylphenol <0.01 <0.01 mg/kg TM16/PM8

2-Nitrophenol <0.01 <0.01 mg/kg TM16/PM8

2,4-Dichlorophenol <0.01 <0.01 mg/kg TM16/PM8

2,4-Dimethylphenol <0.01 <0.01 mg/kg TM16/PM8

2,4,5-Trichlorophenol <0.01 <0.01 mg/kg TM16/PM8

2,4,6-Trichlorophenol <0.01 <0.01 mg/kg TM16/PM8

4-Chloro-3-methylphenol <0.01 <0.01 mg/kg TM16/PM8

4-Methylphenol 0.04 <0.01 mg/kg TM16/PM8

4-Nitrophenol <0.01 <0.01 mg/kg TM16/PM8

Pentachlorophenol <0.01 <0.01 mg/kg TM16/PM8

Phenol <0.01 <0.01 mg/kg TM16/PM8

PAHs

2-Chloronaphthalene <0.01 <0.01 mg/kg TM16/PM8

2-Methylnaphthalene 0.04 <0.01 mg/kg TM16/PM8

Naphthalene <0.01 <0.01 mg/kg TM16/PM8

Acenaphthylene <0.01 <0.01 mg/kg TM16/PM8

Acenaphthene <0.01 <0.01 mg/kg TM16/PM8

Fluorene <0.01 <0.01 mg/kg TM16/PM8

Phenanthrene 0.05 <0.01 mg/kg TM16/PM8

Anthracene <0.01 <0.01 mg/kg TM16/PM8

Fluoranthene <0.01 <0.01 mg/kg TM16/PM8

Pyrene 0.02 <0.01 mg/kg TM16/PM8

Benzo(a)anthracene <0.01 <0.01 mg/kg TM16/PM8

Chrysene <0.01 <0.01 mg/kg TM16/PM8

Benzo(bk)fluoranthene <0.01 <0.01 mg/kg TM16/PM8

Benzo(a)pyrene <0.01 <0.01 mg/kg TM16/PM8

Indeno(123cd)pyrene <0.01 <0.01 mg/kg TM16/PM8

Dibenzo(ah)anthracene <0.01 <0.01 mg/kg TM16/PM8

Benzo(ghi)perylene <0.01 <0.01 mg/kg TM16/PM8

Phthalates

Bis(2-ethylhexyl) phthalate 1.52 <0.01 mg/kg TM16/PM8

Butylbenzyl phthalate <0.01 <0.01 mg/kg TM16/PM8

Di-n-butyl phthalate <0.01 <0.01 mg/kg TM16/PM8

Di-n-Octyl phthalate <0.01 <0.01 mg/kg TM16/PM8

Diethyl phthalate <0.01 <0.01 mg/kg TM16/PM8

Dimethyl phthalate <0.01 <0.01 mg/kg TM16/PM8

Jones Environmental Laboratory

Kishon Project

David Adams

Please see attached notes for all

abbreviations and acronyms

LOD UnitsMethod

No.

QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 4 of 7

Page 53: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

Client Name: SVOC Report : Solid

Reference:

Location:

Contact:

JE Job No.: 15/691

J E Sample No. 1

Sample ID K3786

Depth

COC No / misc VS-101115-L4-1

Containers T

Sample Date 11/10/2015

Sample Type Solid

Batch Number 1

Date of Receipt 11/10/2015

SVOC MS

Other SVOCs

1,2-Dichlorobenzene <0.01 <0.01 mg/kg TM16/PM8

1,2,4-Trichlorobenzene <0.01 <0.01 mg/kg TM16/PM8

1,3-Dichlorobenzene <0.01 <0.01 mg/kg TM16/PM8

1,4-Dichlorobenzene <0.01 <0.01 mg/kg TM16/PM8

2-Nitroaniline <0.01 <0.01 mg/kg TM16/PM8

2,4-Dinitrotoluene <0.01 <0.01 mg/kg TM16/PM8

2,6-Dinitrotoluene <0.01 <0.01 mg/kg TM16/PM8

3-Nitroaniline <0.01 <0.01 mg/kg TM16/PM8

4-Bromophenylphenylether <0.01 <0.01 mg/kg TM16/PM8

4-Chloroaniline <0.01 <0.01 mg/kg TM16/PM8

4-Chlorophenylphenylether <0.01 <0.01 mg/kg TM16/PM8

4-Nitroaniline <0.01 <0.01 mg/kg TM16/PM8

Azobenzene <0.01 <0.01 mg/kg TM16/PM8

Bis(2-chloroethoxy)methane <0.01 <0.01 mg/kg TM16/PM8

Bis(2-chloroethyl)ether <0.01 <0.01 mg/kg TM16/PM8

Carbazole <0.01 <0.01 mg/kg TM16/PM8

Dibenzofuran <0.01 <0.01 mg/kg TM16/PM8

Hexachlorobenzene <0.01 <0.01 mg/kg TM16/PM8

Hexachlorobutadiene <0.01 <0.01 mg/kg TM16/PM8

Hexachlorocyclopentadiene <0.01 <0.01 mg/kg TM16/PM8

Hexachloroethane <0.01 <0.01 mg/kg TM16/PM8

Isophorone <0.01 <0.01 mg/kg TM16/PM8

N-nitrosodi-n-propylamine <0.01 <0.01 mg/kg TM16/PM8

Nitrobenzene <0.01 <0.01 mg/kg TM16/PM8

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

Please see attached notes for all

abbreviations and acronyms

QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 5 of 7

Page 54: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

Client Name: VOC Report : Solid

Reference:

Location:

Contact:

JE Job No.: 15/691

J E Sample No. 1

Sample ID K3786

Depth

COC No / misc VS-101115-L4-1

Containers T

Sample Date 11/10/2015

Sample Type Solid

Batch Number 1

Date of Receipt 11/10/2015

VOC MS

Dichlorodifluoromethane <0.002 <0.002 mg/kg TM15/PM10

Methyl Tertiary Butyl Ether <0.002 <0.002 mg/kg TM15/PM10

Chloromethane <0.003 <0.003 mg/kg TM15/PM10

Vinyl Chloride <0.002 <0.002 mg/kg TM15/PM10

Bromomethane <0.001 <0.001 mg/kg TM15/PM10

Chloroethane <0.002 <0.002 mg/kg TM15/PM10

Trichlorofluoromethane <0.002 <0.002 mg/kg TM15/PM10

1,1-Dichloroethene (1,1 DCE) <0.006 <0.006 mg/kg TM15/PM10

Dichloromethane (DCM) <0.007 <0.007 mg/kg TM15/PM10

trans-1-2-Dichloroethene <0.003 <0.003 mg/kg TM15/PM10

1,1-Dichloroethane <0.003 <0.003 mg/kg TM15/PM10

cis-1-2-Dichloroethene <0.003 <0.003 mg/kg TM15/PM10

2,2-Dichloropropane <0.004 <0.004 mg/kg TM15/PM10

Bromochloromethane <0.003 <0.003 mg/kg TM15/PM10

Chloroform <0.003 <0.003 mg/kg TM15/PM10

1,1,1-Trichloroethane <0.003 <0.003 mg/kg TM15/PM10

1,1-Dichloropropene <0.003 <0.003 mg/kg TM15/PM10

Carbon tetrachloride <0.004 <0.004 mg/kg TM15/PM10

1,2-Dichloroethane <0.004 <0.004 mg/kg TM15/PM10

Benzene <0.003 <0.003 mg/kg TM15/PM10

Trichloroethene (TCE) <0.003 <0.003 mg/kg TM15/PM10

1,2-Dichloropropane <0.006 <0.006 mg/kg TM15/PM10

Dibromomethane <0.003 <0.003 mg/kg TM15/PM10

Bromodichloromethane <0.003 <0.003 mg/kg TM15/PM10

cis-1-3-Dichloropropene <0.004 <0.004 mg/kg TM15/PM10

Toluene <0.003 <0.003 mg/kg TM15/PM10

trans-1-3-Dichloropropene <0.003 <0.003 mg/kg TM15/PM10

1,1,2-Trichloroethane <0.003 <0.003 mg/kg TM15/PM10

Tetrachloroethene (PCE) <0.003 <0.003 mg/kg TM15/PM10

1,3-Dichloropropane <0.003 <0.003 mg/kg TM15/PM10

Dibromochloromethane <0.003 <0.003 mg/kg TM15/PM10

1,2-Dibromoethane <0.003 <0.003 mg/kg TM15/PM10

Chlorobenzene <0.003 <0.003 mg/kg TM15/PM10

1,1,1,2-Tetrachloroethane <0.003 <0.003 mg/kg TM15/PM10

Ethylbenzene 0.041 <0.003 mg/kg TM15/PM10

p/m-Xylene 0.059 <0.006 mg/kg TM15/PM10

o-Xylene 0.024 <0.003 mg/kg TM15/PM10

Styrene <0.003 <0.003 mg/kg TM15/PM10

Bromoform <0.003 <0.003 mg/kg TM15/PM10

Isopropylbenzene 0.022 <0.003 mg/kg TM15/PM10

1,1,2,2-Tetrachloroethane <0.003 <0.003 mg/kg TM15/PM10

Bromobenzene <0.002 <0.002 mg/kg TM15/PM10

1,2,3-Trichloropropane <0.004 <0.004 mg/kg TM15/PM10

Propylbenzene <0.004 <0.004 mg/kg TM15/PM10

2-Chlorotoluene <0.003 <0.003 mg/kg TM15/PM10

1,3,5-Trimethylbenzene <0.003 <0.003 mg/kg TM15/PM10

4-Chlorotoluene <0.003 <0.003 mg/kg TM15/PM10

tert-Butylbenzene <0.005 <0.005 mg/kg TM15/PM10

1,2,4-Trimethylbenzene 0.110 <0.006 mg/kg TM15/PM10

sec-Butylbenzene <0.004 <0.004 mg/kg TM15/PM10

4-Isopropyltoluene 0.108 <0.004 mg/kg TM15/PM10

1,3-Dichlorobenzene <0.004 <0.004 mg/kg TM15/PM10

1,4-Dichlorobenzene <0.004 <0.004 mg/kg TM15/PM10

n-Butylbenzene 0.116 <0.004 mg/kg TM15/PM10

1,2-Dichlorobenzene <0.004 <0.004 mg/kg TM15/PM10

1,2-Dibromo-3-chloropropane <0.004 <0.004 mg/kg TM15/PM10

1,2,4-Trichlorobenzene <0.007 <0.007 mg/kg TM15/PM10

Hexachlorobutadiene <0.004 <0.004 mg/kg TM15/PM10

Naphthalene <0.027 <0.027 mg/kg TM15/PM10

1,2,3-Trichlorobenzene <0.007 <0.007 mg/kg TM15/PM10

Surrogate Recovery Toluene D8 72 <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 36 <0 % TM15/PM10

Please see attached notes for all

abbreviations and acronyms

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

QF-PM 3.1.4 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 6 of 7

Page 55: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

NOTE

JE Job No.:

#

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

CO

OC

NFD

Calibrated against a single substance.

No Determination Possible

ABBREVIATIONS and ACRONYMS USED

No Asbestos Detected.

None Detected (usually refers to VOC and/SVOC TICs).

UKAS accredited.

If you have not already done so, please send us a purchase order if this is required by your company.

All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless

otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.

No Fibres Detected

Result outside calibration range, results should be considered as indicative only and are not accredited.

Results expressed on as received basis.

Surrogate recovery outside performance criteria. This may be due to a matrix effect.

Data is only accredited when all the requirements of our Quality System have been met. In certain circumstances where the requirements have not

been met, the laboratory may issue the data in an interim report but will remove the accreditation, in this instance results should be considered

indicative only. Where possible samples will be re-extracted and a final report issued with accredited results. Please do not hesitate to contact the

laboratory if further details are required of the circumstances which have led to the removal of accreditation.

Dilution required.

Indicates analyte found in associated method blank.

Not applicable

MCERTS accredited.

AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.

Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to peat,

clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids. Acceptable

limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance criteria but the

associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.

Analysis subcontracted to a Jones Environmental approved laboratory.

Outside Calibration Range

Suspected carry over

NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS

Please note we are only MCERTS accredited for sand, loam and clay and any other matrix is outside our scope of accreditation.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

15/691

WATERS

15/691

Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our

MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations of

them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS

accredited.

All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary. If we are instructed to keep samples, a

storage charge of £1 (1.5 Euros) per sample per month will be applied until we are asked to dispose of them.

It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be

included unless we are requested to remove them.

UKAS accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are outside our

scope of accreditation

As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting samples.

Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable

containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and

any test results that may be compromised highlighted on your deviating samples report.

Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.

Please note we are not a Drinking Water Inspectorate (DWI) Approved Laboratory . It is important that detection limits are carefully considered when

requesting water analysis.

QF-PM 3.1.9 v25Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 7 of 7

Page 56: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

Ha’Ashlag 27

Haifa

Israel

3295163

Kishon Project

Attention :

Date :

Your reference :

Our reference :

Location :

Date samples received :

Status :

Issue :

Three samples were received for analysis on 13th October, 2015. Please find attached our Test Report which should be read with notes at the end

of the report and should include all sections if reproduced. Interpretations and opinions are outside the scope of any accreditation, and all results

relate only to samples supplied.

All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.

Dave Adams

Site Scientist

18th October, 2015

13th October, 2015

Final report

Compiled By:

Test Report 15/692 Batch 1 Schedule A

1

David Adams

Haifa

Israel

Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK

Jones Environmental Laboratory

Tel: +972 58 401 0455

QF-PM 3.1.1 v15Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 7

Page 57: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

Client Name: Report : Solid

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 15/692

J E Sample No. 1 2 3

Sample ID K3787 K3788-1 K3788-2

Depth

COC No / misc VS-101215-L4-1 VS-101315-L4-1 VS-101315-L4-1

Containers T T T

Sample Date 13/10/2015 13/10/2015 13/10/2015

Sample Type Solid Solid Solid

Batch Number 1 1 1

Date of Receipt 13/10/2015 13/10/2015 13/10/2015

TPH CWG

Aliphatics

>C5-C6 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>C6-C8 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>C8-C10 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>C10-C12 <0.2 0.9 <0.2 <0.2 mg/kg TM5/PM16

>C12-C16 <4 26 19 <4 mg/kg TM5/PM16

>C16-C21 <7 86 64 <7 mg/kg TM5/PM16

>C21-C35 35 207 157 <7 mg/kg TM5/PM16

>C35-C44 <7 30 23 <7 mg/kg TM5/PM16

Total aliphatics C5-44 35 350 263 <26 mg/kg TM5/TM36/PM16

Aromatics

>C5-EC7 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>EC7-EC8 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>EC8-EC10 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12

>EC10-EC12 <0.2 <0.2 <0.2 <0.2 mg/kg TM5/PM16

>EC12-EC16 <4 <4 <4 <4 mg/kg TM5/PM16

>EC16-EC21 <7 21 20 <7 mg/kg TM5/PM16

>EC21-EC35 36 117 121 <7 mg/kg TM5/PM16

>EC35-EC44 <7 18 25 <7 mg/kg TM5/PM16

Total aromatics C5-44 36 156 166 <26 mg/kg TM5/TM36/PM16

Total aliphatics and aromatics(C5-44) 71 506 429 <52 mg/kg TM5/TM36/PM16

Natural Moisture Content 19.7 17.2 17.2 <0.1 % PM4/PM0

Moisture Content 16.4 14.7 14.7 <0.1 % PM4/PM0

pH 8.03 7.81 7.76 <0.01 pH units TM19/PM11

Please see attached notes for all

abbreviations and acronyms

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

QF-PM 3.1.2 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 7

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Client Name: SVOC Report : Solid

Reference:

Location:

Contact:

JE Job No.: 15/692

J E Sample No. 1 2 3

Sample ID K3787 K3788-1 K3788-2

Depth

COC No / misc VS-101215-L4-1 VS-101315-L4-1 VS-101315-L4-1

Containers T T T

Sample Date 13/10/2015 13/10/2015 13/10/2015

Sample Type Solid Solid Solid

Batch Number 1 1 1

Date of Receipt 13/10/2015 13/10/2015 13/10/2015

SVOC MS

Phenols

2-Chlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2-Methylphenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2-Nitrophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2,4-Dichlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2,4-Dimethylphenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2,4,5-Trichlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2,4,6-Trichlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

4-Chloro-3-methylphenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

4-Methylphenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

4-Nitrophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Pentachlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Phenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

PAHs

2-Chloronaphthalene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2-Methylnaphthalene <0.01 <0.01 0.01 <0.01 mg/kg TM16/PM8

Naphthalene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Acenaphthylene <0.01 <0.01 0.02 <0.01 mg/kg TM16/PM8

Acenaphthene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Fluorene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Phenanthrene <0.01 0.02 0.03 <0.01 mg/kg TM16/PM8

Anthracene <0.01 <0.01 0.01 <0.01 mg/kg TM16/PM8

Fluoranthene <0.01 0.02 0.02 <0.01 mg/kg TM16/PM8

Pyrene 0.02 0.04 0.05 <0.01 mg/kg TM16/PM8

Benzo(a)anthracene 0.05 0.03 0.04 <0.01 mg/kg TM16/PM8

Chrysene <0.01 0.03 0.04 <0.01 mg/kg TM16/PM8

Benzo(bk)fluoranthene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Benzo(a)pyrene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Indeno(123cd)pyrene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Dibenzo(ah)anthracene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Benzo(ghi)perylene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Phthalates

Bis(2-ethylhexyl) phthalate <0.01 1.11 1.34 <0.01 mg/kg TM16/PM8

Butylbenzyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Di-n-butyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Di-n-Octyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Diethyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Dimethyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Please see attached notes for all

abbreviations and acronyms

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 7

Page 59: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

Client Name: SVOC Report : Solid

Reference:

Location:

Contact:

JE Job No.: 15/692

J E Sample No. 1 2 3

Sample ID K3787 K3788-1 K3788-2

Depth

COC No / misc VS-101215-L4-1 VS-101315-L4-1 VS-101315-L4-1

Containers T T T

Sample Date 13/10/2015 13/10/2015 13/10/2015

Sample Type Solid Solid Solid

Batch Number 1 1 1

Date of Receipt 13/10/2015 13/10/2015 13/10/2015

SVOC MS

Other SVOCs

1,2-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

1,2,4-Trichlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

1,3-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

1,4-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2-Nitroaniline <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2,4-Dinitrotoluene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

2,6-Dinitrotoluene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

3-Nitroaniline <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

4-Bromophenylphenylether <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

4-Chloroaniline <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

4-Chlorophenylphenylether <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

4-Nitroaniline <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Azobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Bis(2-chloroethoxy)methane <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Bis(2-chloroethyl)ether <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Carbazole <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Dibenzofuran <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Hexachlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Hexachlorobutadiene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Hexachlorocyclopentadiene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Hexachloroethane <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Isophorone <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

N-nitrosodi-n-propylamine <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

Nitrobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

Please see attached notes for all

abbreviations and acronyms

QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 4 of 7

Page 60: V1-V7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ..... ילהנמ םוכיס

Client Name: VOC Report : Solid

Reference:

Location:

Contact:

JE Job No.: 15/692

J E Sample No. 1 2 3

Sample ID K3787 K3788-1 K3788-2

Depth

COC No / misc VS-101215-L4-1 VS-101315-L4-1 VS-101315-L4-1

Containers T T T

Sample Date 13/10/2015 13/10/2015 13/10/2015

Sample Type Solid Solid Solid

Batch Number 1 1 1

Date of Receipt 13/10/2015 13/10/2015 13/10/2015

VOC MS

Dichlorodifluoromethane <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10

Methyl Tertiary Butyl Ether <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10

Chloromethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Vinyl Chloride <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10

Bromomethane <0.001 <0.001 <0.001 <0.001 mg/kg TM15/PM10

Chloroethane <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10

Trichlorofluoromethane <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10

1,1-Dichloroethene (1,1 DCE) <0.006 <0.006 <0.006 <0.006 mg/kg TM15/PM10

Dichloromethane (DCM) <0.007 <0.007 <0.007 <0.007 mg/kg TM15/PM10

trans-1-2-Dichloroethene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,1-Dichloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

cis-1-2-Dichloroethene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

2,2-Dichloropropane <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

Bromochloromethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Chloroform <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,1,1-Trichloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,1-Dichloropropene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Carbon tetrachloride <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

1,2-Dichloroethane <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

Benzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Trichloroethene (TCE) <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,2-Dichloropropane <0.006 <0.006 <0.006 <0.006 mg/kg TM15/PM10

Dibromomethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Bromodichloromethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

cis-1-3-Dichloropropene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

Toluene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

trans-1-3-Dichloropropene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,1,2-Trichloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Tetrachloroethene (PCE) <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,3-Dichloropropane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Dibromochloromethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,2-Dibromoethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Chlorobenzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,1,1,2-Tetrachloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Ethylbenzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

p/m-Xylene <0.006 <0.006 <0.006 <0.006 mg/kg TM15/PM10

o-Xylene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Styrene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Bromoform <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Isopropylbenzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,1,2,2-Tetrachloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

Bromobenzene <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10

1,2,3-Trichloropropane <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

Propylbenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

2-Chlorotoluene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

1,3,5-Trimethylbenzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

4-Chlorotoluene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10

tert-Butylbenzene <0.005 <0.005 <0.005 <0.005 mg/kg TM15/PM10

1,2,4-Trimethylbenzene <0.006 <0.006 <0.006 <0.006 mg/kg TM15/PM10

sec-Butylbenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

4-Isopropyltoluene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

1,3-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

1,4-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

n-Butylbenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

1,2-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

1,2-Dibromo-3-chloropropane <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

1,2,4-Trichlorobenzene <0.007 <0.007 <0.007 <0.007 mg/kg TM15/PM10

Hexachlorobutadiene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10

Naphthalene <0.027 <0.027 <0.027 <0.027 mg/kg TM15/PM10

1,2,3-Trichlorobenzene <0.007 <0.007 <0.007 <0.007 mg/kg TM15/PM10

Surrogate Recovery Toluene D8 108 103 96 <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 92 77 65 <0 % TM15/PM10

Please see attached notes for all

abbreviations and acronyms

LOD UnitsMethod

No.

Jones Environmental Laboratory

Kishon Project

David Adams

QF-PM 3.1.4 v10Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 5 of 7

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JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

NOTE

JE Job No.:

#

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

CO

OC

NFD

Outside Calibration Range

Suspected carry over

NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS

Please note we are only MCERTS accredited for sand, loam and clay and any other matrix is outside our scope of accreditation.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

15/692

WATERS

15/692

Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our

MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations of

them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS

accredited.

All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary. If we are instructed to keep samples, a

storage charge of £1 (1.5 Euros) per sample per month will be applied until we are asked to dispose of them.

It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be

included unless we are requested to remove them.

UKAS accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are outside our

scope of accreditation

As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting samples.

Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable

containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and

any test results that may be compromised highlighted on your deviating samples report.

Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.

Please note we are not a Drinking Water Inspectorate (DWI) Approved Laboratory . It is important that detection limits are carefully considered when

requesting water analysis.

If you have not already done so, please send us a purchase order if this is required by your company.

All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless

otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.

No Fibres Detected

Result outside calibration range, results should be considered as indicative only and are not accredited.

Results expressed on as received basis.

Surrogate recovery outside performance criteria. This may be due to a matrix effect.

Data is only accredited when all the requirements of our Quality System have been met. In certain circumstances where the requirements have not

been met, the laboratory may issue the data in an interim report but will remove the accreditation, in this instance results should be considered

indicative only. Where possible samples will be re-extracted and a final report issued with accredited results. Please do not hesitate to contact the

laboratory if further details are required of the circumstances which have led to the removal of accreditation.

Dilution required.

Indicates analyte found in associated method blank.

Not applicable

MCERTS accredited.

AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.

Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to peat,

clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids. Acceptable

limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance criteria but the

associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.

Analysis subcontracted to a Jones Environmental approved laboratory.

Calibrated against a single substance.

No Determination Possible

ABBREVIATIONS and ACRONYMS USED

No Asbestos Detected.

None Detected (usually refers to VOC and/SVOC TICs).

UKAS accredited.

QF-PM 3.1.9 v25Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 6 of 7

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JE Job No: 15/692

Test Method No. Description

Prep Method

No. (if

appropriate)

Description UKAS

MCERTS

(soils

only)

Analysis done on

As Received

(AR) or Air Dried

(AD)

Reported on

dry weight

basis

PM4Gravimetric measurement of Natural Moisture Content and % Moisture Content at either

35°C or 105°C. Calculation based on ISO 11465 and BS1377.PM0 No preparation is required.

TM5

In-House method based on USEPA 8015B. Determination of Extractable Petroleum

Hydrocarbons (EPH) in the carbon chain length range of C8-40 by GC-FID. Accredited to

ISO 17025 on soil and water samples and MCERTS (carbon banding only) on soils. All

accreditation is matrix specific.

PM16 Aliphatic/Aromatic fractionation AR Yes

TM5/TM36 TPH CWG by GC-FID PM16 Aliphatic/Aromatic fractionation AR Yes

TM15

In-House method based on USEPA 8260. Determination of Volatile Organic compounds

(VOCs) by Headspace GC-MS. Accredited to ISO 17025 for soils and waters and

MCERTS for Soils. All accreditation is matrix specific. Quantification by Internal Standard

method.

PM10

In-house method based on USEPA 5021. Preparation of solid and liquid samples for

headspace analysis. Samples are spiked with surrogates to facilitate quantification. ISO

17025 accredited extraction method. All accreditation is matrix specific

AR Yes

TM16

In-House method based on USEPA 8270. Determination of Semi-Volatile Organic

compounds (SVOCs) by GC-MS. Accredited to ISO 17025 for waters. All accreditation is

matrix specific. Quantification by Internal Standard method.

PM8In-house method based on USEPA 3510. ISO 17025 accredited extraction method for

organic extraction from solid samples using an end over end agitator.AR Yes

TM19 pH by meter PM11 1:2.5 soil/water extraction AR No

TM36

In-House method based on USEPA 8015B. Determination of Gasoline Range Organics

(GRO) in the carbon chain range of C5-12 by headspace GC-FID. Accredited to ISO

17025 on soil and water samples and MCERTS accredited (carbon banding only) on

soils. All accreditation is matrix specific.

PM12

In-house method based on USEPA 5021. Preparation of solid and liquid samples for

headspace analysis. Samples are spiked with surrogates to facilitate quantification. ISO

17025 accredited extraction method. All accreditation is matrix specific

AR Yes

Jones Environmental Laboratory Method Code Appendix

QF-PM 3.1.10 v13 Please include all sections of this report if it is reproduced 7 of 7

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Ha’Ashlag 27

Haifa

Israel

3295163

Kishon Project

Attention :

Date :

Your reference :

Our reference :

Location :

Date samples received :

Status :

Issue :

David Adams

Haifa

Israel

Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK

Jones Environmental Laboratory

Tel: +972 58 401 0455

One sample were received for analysis on 15th October, 2015. Please find attached our Test Report which should be read with notes at the end of

the report and should include all sections if reproduced. Interpretations and opinions are outside the scope of any accreditation, and all results relate

only to samples supplied.

All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.

Dave Adams

Site Scientist

19th October, 2015

15th October, 2015

Final report

Compiled By:

Test Report 15/693 Batch 1

1

QF-PM 3.1.1 v15Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 1