modeling the risk of toxicity in brain tumor patients ... universit a degli studi di trento...

80
Universit` a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in brain tumor patients treated with protons Supervisor Dr. Francesco Tommasino Student Alberto Taffelli

Upload: others

Post on 17-Apr-2020

1 views

Category:

Documents


0 download

TRANSCRIPT

Page 1: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Universita degli Studi di Trento

DEPARTMENT OF PHYSICS

Master’s degreeA.Y. 2017-2018

Modeling the risk of toxicity in braintumor patients treated with protons

Supervisor

Dr. Francesco Tommasino

Student

Alberto Taffelli

Page 2: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Abstract

Page 3: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Contents

1 Physics and radiobiology of protontherapy 51.1 Proton interaction with matter . . . . . . . . . . . . . . . . . 6

1.1.1 Stopping power and Bethe-Block equation . . . . . . . 61.1.2 Depth dose curve and Bragg peak . . . . . . . . . . . . 11

1.2 Biological damage . . . . . . . . . . . . . . . . . . . . . . . . . 131.2.1 Biological damage of ionizing particles . . . . . . . . . 131.2.2 RBE . . . . . . . . . . . . . . . . . . . . . . . . . . . . 18

1.3 TCP and NTCP modelling . . . . . . . . . . . . . . . . . . . . 211.3.1 TCP . . . . . . . . . . . . . . . . . . . . . . . . . . . . 211.3.2 NTCP . . . . . . . . . . . . . . . . . . . . . . . . . . . 23

1.4 Monte Carlo beam transport simulation . . . . . . . . . . . . . 271.4.1 GEANT4 . . . . . . . . . . . . . . . . . . . . . . . . . 29

2 Material and Methods 302.1 Materials . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 31

2.1.1 Trento proton center facility . . . . . . . . . . . . . . . 312.1.2 Patients and outcome . . . . . . . . . . . . . . . . . . . 34

2.2 Method . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 352.2.1 Dose metrics extraction . . . . . . . . . . . . . . . . . 352.2.2 Statistical analysis and NTCP model . . . . . . . . . . 382.2.3 RBE weighted dose maps recalculation . . . . . . . . . 41

3 Results and discussion 483.1 Statistical analysis . . . . . . . . . . . . . . . . . . . . . . . . 48

3.1.1 RIF and RIA Outcomes . . . . . . . . . . . . . . . . . 483.1.2 RIF analysis . . . . . . . . . . . . . . . . . . . . . . . . 493.1.3 RIA analysis . . . . . . . . . . . . . . . . . . . . . . . . 51

3.2 RBE maps . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 57

1

Page 4: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

3.2.1 LET validation . . . . . . . . . . . . . . . . . . . . . . 573.2.2 Application to a patient subset . . . . . . . . . . . . . 62

4 Conclusions 67

2

Page 5: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Introduction

Radiotherapy for treating tumors is spread nowadays all around the world.About 50% of the cancer treatments rely on radiotherapy, but this is oneof the possible therapies of the larger family of the cancer treatments, towhich also chemotherapy and surgery belong. They are often used also incombination in order to improve the effect of the treatment (e.g. chemother-apy and radiotherapy). The idea of radiotherapy is to exploit the damagethat ionizing radiations can induce at the molecular level in order to inducecell damage and death. Beams of radiation are generated to release dose totumor masses and different technologies are exploited in order to achieve thebest tumor (target) covering and the best healthy tissue sparing.In particular, the proton therapy (PT) is the most diffused alternative to themore conventional and widespread radiotherapy with photons. The use ofprotons for radiotherapy started to spread in the 90’ and it is now diffusedall over the world with over 50 operating proton therapy centers [1] and over150000 patients treated [2].In Trento (I), a proton therapy center is operating since 2014 and has sofar treated more than 300 patients. Patients generally benefit from protonscompared to photons for what concerns healthy tissue sparing and targetcovering. In fact dose deposited by charged particles within a medium, isdescribed by a sharped peaked curve compared to photons (Fig. 1.1), whichcan be exploited to focus the dose released, making protons suitable for ra-diotherapy. Nevertheless some potential drawbacks have to be considered;for instance, dose deposited to the skin is generally higher in a proton ther-apy treatment, due to the contribution of several single energy beams thatare added together to build the spread out Bragg peak (SOBP) when treat-ing extended regions. This may induce toxicity events during and after thetreatment concerning skin, such as alopecia, dermatitis, necrosis.Furthermore, charged particles, in addition to a physical gain, take advan-

3

Page 6: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

tage of an enhanced biological effect compared to photons, quantified by therelative biological effectiveness (RBE) parameter which is generally maxi-mized when particles are near to stop. This effect, which is significant forheavy ions, is slighter for protons, but, if not considered in a proper way,may underestimate the dose released on different structures, generally themore inner organs located in the distal part of the beam. Therefore, eventhough in clinics a constant value of RBE is assumed, more accurate modelsdescribing the RBE parameter are required to take into account variation inthe biological response to radiation.Toxicities induced by radiation may affect the quality of life of patients (QoL)undergoing radiotherapy, in particular when the disease is permanent. There-fore, models able to describe the risk of developing certain toxicities afterradiotherapy treatment are needed. About this, normal tissue complicationprobability (NTCP) models have been derived for several organs and end-points. However, as a relatively recent cancer treatment approach, protontherapy still leaks of NTCP models describing the risk of developing certainradiation induced toxicities.Aim of this work is thus to find dosimetric variables, able to predict the onsetof radiation inducecd alopecia (RIA) and radiation induced fatigue (RIF), as-sessing a database of patients treated at the proton therapy facility of Trentowith proton therapy for brain tumors (BT). For this purpose, NTCP modelsbased on multivariate logistic regression are developed.

Therefore the thesis is organized as follows:

1. A general introduction on the proton therapy, concerning the physicsof protons and the radiobiology.

2. A detailed chapter on the data set and method used in the study

3. A chapter presenting the results and discussion of the work

4. A final part with conclusions about the work and possible outlook

4

Page 7: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Chapter 1

Physics and radiobiology ofprotontherapy

Figure 1.1: Comparison of depth-dose curves for various particles (photon,proton, carbon ion). The peculiar Bragg peak for both ion types and theirdifferences are clearly visible. Image taken from [3].

This chapter is intended to give basic principles of proton therapy andin particular the tools to comprehend the work. Therefore, a first sectionwill be dedicated to the physics of protons interacting with matter, movingfrom the microscopic nature of the interaction, to the macroscopic effectwhen looking on the dose deposited within the medium, which gives the

5

Page 8: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

typical peaked depth dose curve for charged particles (Fig. 1.1). Moreover asection will be dedicated to the radiobiology, i.e. the biological response toradiation, starting from the damage induced by radiation to cells, and thenintroducing the concept of RBE to describe the response of cells and tissuesto different radiation types, and how this parameter is considered in clinic.Furthermore a paragraph will highlight features of tumor control probability(TCP) models and normal tissue complication probability (NTCP) modeladopted in order to have a clinical significant predictive quantity for a givenirradiation schedule (treatment plan). Finally an introduction to the MonteCarlo methods for simulations which have been exploited in this work willbe given at the end of this chapter.

1.1 Proton interaction with matter

While protons travel trough the absorbing medium, they can experience threedistinct types of interactions (Fig.1.2): they can slow down (stopping) bymultiple collisions with atomic and molecular electrons, leading to excitationand ionization of the medium, they can be deflected (scattering) by multipleCoulomb collisions with the atomic nuclei, and finally can have an head-oncollision with nuclei (nuclear interactions) that can result in the productionof γ-rays, neutrons n or ions ([4]). To a first-order approximation, protonscontinuously lose kinetic energy via frequent inelastic collision with atomicelectrons. They travel nearly straight since their mass is 103 times the massof the electrons. Differently, when a proton passes near the nucleus it expe-riences a repulsive force that deflects its trajectory due to the large mass ofthe nucleus. Inelastic nuclear reactions between proton and the nucleus areless frequent, but may lead to target fragmentation via emission of protonsor heavier ions. Eventually Bremsstrahlung is also a theoretically possibleprocess, but at the energies used for therapeutic application, it is unlikely tohappen [5].

1.1.1 Stopping power and Bethe-Block equation

The energy transfer from an ion to matter in each individual atomic inter-action is generally small, so that the particle undergoes a large number ofinteractions before its kinetic energy is spent. Stopping power is the param-eter used to describe the gradual loss of energy of the charged particle as it

6

Page 9: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.2: Three different types of collisions of a proton with an atom.Inelastic collision via electromagnetic interaction with an orbital electron(a); elastic collision via electromagnetic interaction with the atomic nucleus(b); and inelastic collision via nuclear interaction with production of gammarays γ, neutrons n or alpha particles (c) [5].

7

Page 10: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

penetrates into an absorbing medium. Two classes of stopping powers areknown: the collision stopping power Scol which can be electronic, due to theCoulomb interaction of the incident ions with the electrons of the traversedmaterial, or nuclear, due to the Coulomb interactions with the nuclei , andthe radiative stopping power, related to the emission of radiation in the elec-tric field of atomic nuclei or atomic electrons.The rate of energy loss by the charged particle per unit length (-dE/dx) inthe medium is called linear stopping power and it is dependent on both par-ticle and absorbing medium properties. Generally the stopping power is bestexpressed in MeV cm2/g because it is divided by the density ρ = g/cm3 ofthe absorber in order to remove its dependence (Mass stopping power). Theenergy loss is given by both collision loss and radiative loss contributions, sothat the total stopping power is Stot = Srad + Scol.The formulation of the mass stopping power was developed by Bethe andBlock in 1933 and has its relativistic expression in the formula:

Sρ = −dEdx

= 4πNAr2emec

2Z

A

z2

β2

[ln

2mec2γ2β2

< I >− β2 − δ

2− C

Z

](1.1)

where NA is Avogadro’s number, re is the classical electron radius, me is themass of an electron, Z and A are the atomic number and atomic mass ofthe absorber medium, z is the atomic number of the charged particle and< I > is the mean excitation energy of the target material, namely the meanminimum energy ∆Eexc that can be transferred from the incoming particleto an absorber atom via Coulomb interaction with an orbital electron. < I >is a monotonic increasing function of Z and ranges from 19 eV for hydrogento 820 eV for lead. The last two terms in the equation 1.1, δ and C, are twocorrection terms which involve relativistic theory and quantum mechanicsand need to be considered when protons with high or very low energy areused in calculations.Concerning the dependence of the stopping power from the incoming chargedparticle, we notice that Sρ is proportional to z2, so that in general, heaviernuclei suffer more energy loss for the same β; in addition it is also propor-tional to β−2, meaning that the stopping power increases as the particle slowsdown in the medium (Fig. 1.3). This gives the typical Bragg peak profilealong the penetration direction for a charged particle shown in Fig.1.1. Onthe other hand the dependence on the medium is expressed by the factorZ/A and by the logarithm of I−1.Once the stopping power is known one can calculate the range of a charged

8

Page 11: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.3: Stopping power in water for a proton beam. For energies used intherapy we notice that Sρ is a decreasing function of the energy.[6]

particle with a certain initial kinetic energy inside a medium. This is a funda-mental task in hadron therapy, in order to select the energy of a particle thathas to reach the target (tumor). The range for heavy particles can be calcu-lated with CSDA (continuous slowing down approximation) as suggested byBerger and Seltzer in 1983:

RCSDA(Ek) =

∫ 0

Ekin

− dE

Stot(Ek)(1.2)

In the case of heavy charged particles the CSDA is a good approxima-tion of the average range R of the particle in the medium, because of theiressentially straight path trough the medium compared to that of lightestparticles (e.g. electron, positrons) as shown in Fig.(1.4). Fig.(1.5) shows therange for a proton beam as a function of the energy calculated with CSDAand compared to the range obtained by projecting the path along the beamdirection. We notice that the approximation is reliable in the energy rangerequired to cover the human body size (101-102 MeV). Another quantityused in dosimetry is the LET (Linear Energy Transfer) expressed in keV/µmwhich is defined as the energy released by the ionizing particle per unit length

9

Page 12: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.4: Schematic diagram of charged particle penetration into a medium.Top: Heavy charged particle; bottom: light charged particle (electron orpositron) [7].

to the electrons in the medium (dE/dx). LET differs from linear stoppingpower as the former considers only the electronic collision stopping power,while the latter takes into account also radiative losses and nuclear collisionlosses by electromagnetic interaction. Moreover, LET is normally referringto energy deposited locally and loses the energy transported by secondariesat distant locations. In fact, LET is generally calculated considering energyreleased by primary particles to the secondaries up to a certain threshold.This is defined as the restricted LET (LET∆):

LET∆ =dE∆

dx(1.3)

Which excludes all the secondary particles with energy larger than ∆. Whenwe do not consider restriction in energy of the secondaries, we deal with theunrestricted LET (LET∞) which is equal to minus the electronic collisionstopping power. Nevertheless, at energies considered for therapeutic applica-tion (e.g. protons up to 250 MeV), the LET and the collision stopping powercan be considered to be nearby equal [8].

10

Page 13: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.5: Range of a proton beam in water [6].

1.1.2 Depth dose curve and Bragg peak

In medical applications what we are interested in is the physical absorbeddose D released by a beam of particles in medium. The dose D is defined asthe energy absorbed per unit target mass:

D =dE

dm

[Gy =

J

Kg

](1.4)

Starting from the linear stopping power we can calculate the dose as:

D[Gy] = 1.6 · 10−19 · LET[keV

µm

]· F [cm−2] · 1

ρ

[cm3

g

](1.5)

where LET is the linear energy transfer, F is the fluence of a monoenergeticbeam of particles and ρ is the medium density.Once we know how to calculate the dose from the stopping power and fluence,we can calculate even the dose deposited along a certain depth in a direction(typically the direction of the beam). Fig.(1.6) shows the typical shape ofthe depth dose curve for a proton beam along the beam direction. We notice

11

Page 14: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.6: Left: 75 proton beam depth dose curves calculated with Monte-carlo for energies from 59.4 to 255 MeV [6]. Right: spread out Bragg peak

the presence of a Bragg peak arising by the dependence of the stoppingpower by the inverse of the square velocity of the particle (β−2) in formula(1.1). We notice that this peak has a certain width. When we are performingexperiments or clinical practice we deal with beams of (quasi) monoenergeticparticles directed onto the target and we do not obtain the same exact finiterange for all of them. This phenomenon is the so called range stragglingand it has different causes:

• Energy fluctuations in the incoming beam. Although the beam is nom-inally monoenergetic, there are fluctuation in the spectrum up to 1%that lead to range broadening;

• The nature of the interaction between particles and matter is stochas-tic and this leads to slight variations on energy losses and, as a con-sequence, on the range of the single particle, which increases with thedistance traveled (i.e. as the particle initial energy increases);

We notice from Fig. (1.6) that the Bragg peak has a width of somemillimeters given a certain beam energy. In radiotherapy we deal with tumorswith the extent of several centimeters, thus the use of a single energy beamis not enough to cover with conformity the entire target region. The solutionis the combination of different energy beams that, opportunely weighted inintensity, can cover the region to treat uniformly in the so-called spread outBragg peak (SOBP). A SOBP (Fig. 1.6) has the advantage that we can in

12

Page 15: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.7: Comparison between proton and photon dose depth curves, withparticular emphasis to the entrance dose [9].

principle release a very uniform dose to the target and, thanks to the distalfall off, very low doses to the distal organs at risk (OARs) that may be presentin the patient anatomy. One of the major drawback is instead the increaseof the dose in the entrance channel and thus on the body surface that mayinduce toxicity events related to the skin compared to the conventional useof photons (Fig.1.7).

1.2 Biological damage

In addition to the physical advantage (Bragg peak) discussed in Sec 1.1, theuse of charged particles in cancer treatment can be associated with distinctbiological effects compared to X-ray. Heavy charged particles are consideredhigh LET particles, since the energy released to the medium locally is high,compared to the lighter ones (Eq. 1.1). This property has the consequencethat the ionization path of the charged particle is concentrated in a smalllocalized region (densely ionizing particles) and thus, it is more probable toinduce severe damages at the cellular level [6] (Fig. 1.8).

1.2.1 Biological damage of ionizing particles

Ionizing radiation is able to ionize molecules belonging to sensible structuresinside the cells and the most sensible target to consider is the DNA inside

13

Page 16: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.8: Simulated patterns of DSB distribution after photon and ionirradiation in a typical cell nucleus (radius of ∼ 5µm). Protons are shownat the typical LET assumed in the entrance channel, resulting in a photon-like distribution of lesions (sparsely ionizing radiation). Low energy alphaparticles and oxygen ions are also shown as representative of the typicaltarget fragments produced in PT [10].

14

Page 17: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.9: Types of DNA damages

the cell nucleus. DNA is an helical double strand structure wrapped arounditself to form chromosomes (Fig. 1.9). Chromosomes contain all the geneticinformation of the cell, essential for the cell replication (mitosis). Cells arein general able to repair the majority of damages to the DNA thanks toseveral dedicated proteins. The most severe damage that ionizing radiationcan induce to the DNA is the double strand break (DBS), meaning that boththe helical strands are broken by the radiation. This kind of damage is notalways repairable, and may induce cell death, especially when several of suchdamages are occurring nearby (clustered DSBs). High LET particles, thanksto their dense ionization path, are able to cause more dense DSB damages tothe DNA compared to photons, and thus a major probability to induce celldeath.(Fig. 1.8).Investigation of radiation induced cell death, intended as mitotic death (i.e.loss of proliferation capability) is one of the common methods used to studyeffects of ionizing radiation on cells. Cell lines are irradiated in vitro andthen are seeded in culture flasks at appropriate density; a cell is classified asa survivor if it is able to produce at least 50 daughter cells within a timeinterval of 10-14 cell cycles. Irradiation of cells with different doses lead usto have several experimental points and fit them creating the so called cellsurvival curves which describe the survival fraction of cells as a function ofthe dose.Survival curves can depend in general on different parameters (cell type, cellcycle phase, radiation type, radiation energy, ..) but they all have similar

15

Page 18: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.10: Left: survival curves for normal and sensitive cells. Right:survival curves for different values of α and β. [11]

shape and thus rely on a similar mathematical description. The mathematicalformulation for survival dose response S(D) is based on the so-called linear-quadratic model:

S(D) = S0e−(αD+βD2) (1.6)

Where S0 is the survival probability for unirradiated sample and α and β twoparameters, the former associated to the linear behavior at low doses and thelatter with the quadratic trend at higher doses. Typically what we are inter-ested in is the ratio α/β that determines the trend of the survival curve withthe dose, representing a dose where the linear and quadratic contributions areequal. Each tissue under study is generally labeled by a specific α/β basedon some in vitro or in vivo study, that determines its response to radiation(e.g. a large part of the tumors have an α/β = 10). In Fig.1.10 (left) wenotice that sensitive cells, meaning that they are not proficient in repairingdamages, show a linear trend compared to normal cell’s linear quadratic be-havior. This fact indicates the possibility that the quadratic term in eq.1.6is related to the ability of the cell to repair. Fig.1.10 (right) shows survivalcurves for different values of α and β. The repair of radiation damage takesa certain time interval, thus the damage to a biological object depends alsoon the temporal distribution of the dose delivery: at fixed dose, we expecta larger survival fraction for cell lines exposed to same dose but diluted in

16

Page 19: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.11: Split dose recovery observed after irradiation of two humannormal fibroblast cell lines. The total dose was given in 2 fractions of halfthe total dose with a time interval as indicated on the x-axis [11]

time.It is observed experimentally that the repair capability reaches a saturationwhen the time interval increases 1.11. This indicates that almost all the re-pairable damages have been repaired. This biological behavior is exploitedin radiotherapy, where the dose is typically delivered in several fractions: asan example, a general schedule for a proton therapy treatment could be 30fractions, over 6 weeks, i.e. 5 fractions per week. The advantage of such aschedule is to allow the repair of the healthy tissues surrounding the tumorvolume which receive relatively high doses. In fact tumor cells have in generalless repair capability, so that fractionation has less effect on them. When weare dealing with high LET particles, the LQ model is not more applicable andthe shape of the survival curve is different compared to photons (Fig.1.12).In the logarithmic scale, the survival curve is a straight line, meaning the lossor the attenuation of the quadratic contribution in eq. (1.6). If we assumethat the quadratic contribution is linked to the repair capacity of the cellafter irradiation, as stated above, we can conclude that in the case of highLET radiation, where the damage is more localized and complex, the cell hasmore difficulties in repairing its structures, leading to cell death.

17

Page 20: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

1.2.2 RBE

The way we quantify the enhanced biological effect described in Sec.1.2.1 istrough the RBE (Relative Biological Effectiveness). This factor is defined asthe ratio of absorbed doses, which have to be applied for the two radiationtypes to achieve the same biological effect:

RBE :=Dγ

DI

∣∣∣Isoeffect

(1.7)

Due to their different shape, the survival curves can not be transformed intoeach other by simply applying a constant scaling factor to the dose (dosemodifying factor). When we are dealing with charged particle radiations wecalculate an RBE weighted dose DRBE, in order to account for the enhancedbiological effectiveness, by multiplying the physical absorbed dose for theRBE (DRBE = Dphy ·RBE). Since for high LET particles the survival curvecan be described by a linear term S(D) = S0e

−αD (Fig.1.12), the limit forD > 0 of the RBE is the ratio between the linear coefficients of the survivalcurves:

RBEmax =αγαI

When the dose increases the RBE decreases, down to the value of 1 for veryhigh doses. This asymptotic behavior is in accordance with model of bio-logical damage of radiations described in Sec.1.2.1, since for very high doseswe expect that the damages to the cells reach a saturation and the initialenhanced biological effectiveness of ions compared to photons is reduced.RBE strongly depends on physical characteristics of the particles (e.g. par-ticle charge and LET). The dependence LET is shown in Fig.1.13, where wenotice an initial increase of RBE with the LET and a following saturationtrend. The increase of RBE from low to intermediate LET values can beattributed to increasing energy concentration within the particle tracks; thismay lead to more complex damages into the cell and a consequent increase inthe RBE. The drop of RBE at higher values of LET can instead be explainedconsidering a saturation effect in the damage. RBE is a complex quantityand can in general depend on several parameters: physical (LET, energy,particle type) and biological (cell type, cell cycle phase, oxygenation level)ones.Even if it is clear that the RBE is far from being a constant factor, in proton-therapy clinical practice it is assumed that is more safe to fix its value to 1.1.

18

Page 21: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.12: Explanation of RBE. Experimental data: survival of CHO-K1Chinese hamster cells. (Experimental data from [12])

Figure 1.13: Variation of RBE with linear energy transfer (LET). RBEα

represents the limiting RBE at very low doses, dened by the ratio αI/αX ofthe linear coefficients. (Redrawn from [12] by [11])

19

Page 22: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.14: Physical and RBE-weighted dose are shown, as obtained with aconstant and with a variable RBE. Special emphasis is given to the differencesat the distal fall-off, where OAR might be located [14].

In treatment plans in order to calculate RBE-weighted-dose calculation it isthus enough to increase the physical dose by a 10%, which is quite an easytask and does not require any additional computational power. The reasonis that, despite the moderate experience in the therapeutic use of protons,there is still much to be clarified concerning the biological response of cellsand tissues when irradiated with protons compared to photons, includingtumor and normal tissue response [13]. This is reflected into the large uncer-tainties found in literature in the definition of RBE-LET relation (Fig.1.13).Thus a fixed value of 1.1, based in particular on in vivo results, seems to bea reasonable approximation for different studies [10]. In other words, thismeans that even if the assumption is wrong in principle, there is up to nowno clear clinical evidence against it.Even though clinically accepted, the 1.1 assumption for the RBE of protonsover their whole range may lead to some drawbacks, first of all a possibleunderestimation of the biological dose deposited along the proton path. Thismight cause some extra dose, in particular in the distal fall-off part of thedose depth curve, where the LET of charged particles reaches the maximumand where an OAR might be located (Fig.1.14). Secondly, a complete knowl-

20

Page 23: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

edge of the RBE along the proton range, could allow some dose sparing evenat the level of the treatment plan doses, since we may lower the physical dosewhile fulfilling the same effective dose prescriptions.

1.3 TCP and NTCP modelling

In radiotherapy having models that describe the outcome of a treatment forwhat concerns both the tumor killing and the onset of complications in nor-mal tissues are needed. Therefore tumor control probability (TCP) and nor-mal tissue complication probability (NTCP) models were developed. Thesemodels, as the names suggest, describe the probability to control the tumor,meaning to stop the ability of tumor cell to proliferate, and the probabilityto develop some kind of toxicity in normal tissues, respectively. Such modelsare generally based on dose-volume histograms (DVH) of the different struc-tures inside the body. DVHs represent a compact simplification of the 3Ddose distributions both in target and normal tissues. Each point of the DVHrepresent the volume (relative or absolute) which receives at least a certaindose (Vx is the volume receiving D ≥ x Gy, Fig 1.15, Left). If the NTCPand and TCP vs. prescription doses are computed from their mathematicalexpressions, then shallow curves having sigmoidal shapes result as opposedto a binary situation (Fig.1.15, right).

1.3.1 TCP

Most of the TCP models are mechanistic descriptions that start from thecell survival model, based on the LQ approach for cell damage describedin Sec.1.2. The sigmoidal shape of the dose-response curve (Fig.1.15.Rightpanel) is suitable for a description via Poisson distribution. In 1961, Munroand Gilbert [16] were the first to apply the Poisson statistic to a TCP model.They started from the assumption that the nature of cell damage is stochasticand that a full control of the tumor is obtained when all the malignant cells(clonogens) are not able to proliferate anymore. They derived an expressionfor the probability to control a tumor with N clonogens:

TCP = e−λ (1.8)

where λ is the average number of surviving clonogens.

21

Page 24: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.15: Left: dose-volume histogram (DVH) for clinical target volume(CTV) and organ at risk (OAR). Right: TCP and NTCP vs. prescriptiondose as computed from mathematical functions, whose parameters are de-rived from best fits to DVH-based binary clinical outcomes.[15]

Webb-Nahum’s TCP model

Over the years eq.1.8 has been further developed, allowing the equation toadapt to the new clinical and radiobiological features. In 1993 Webb andNahum [17] proposed a TCP formulation that could benefit from the available3D radiotherapy, where the dose to the tumor is known via DVH. Theymodify equation 1.8 using the LQ model to describe the λ parameter:

TCP = exp(

-N0exp[− αD

(1 +

β

αd)])

(1.9)

where N0 is the initial clonogenic cell number, α and β are the parametersof the LQ model, D = n · d is the total dose given in n fraction of dose d.In order to obtain a more realistic model for the TCP one has to consider

22

Page 25: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

also that experimental data belong to a population of patients with theirindividual radiation sensitivity α distributed normally. Thus:

TCP =K∑i=1

giTCPαi (1.10)

with:gi = exp

[− (αi − αm)2 /2σα

]where αm is the mean value of the radiosensitivity in the interpatient distri-bution, characterised by standard deviation σα.Up to this point it has been assumed that cells receive exactly the same doseD. In order to do this, one needs to how the number of clonogenic cells No,i

that receive a dose Di. This is most conveniently obtained from DVH. Onecan generalize equation 1.9 to:

TCP =1

σα√

∫ ∞0

(∏i

exp(− ρclViexp

[− αDi

(1 +

β

αdi

)]))·

exp[− (αi − αm)2 /2σα

] (1.11)

where i is dose bin in the DVH, ρ, is the clonogenic cell density, V. is thevolume of tissue in the i -th dose bin.

1.3.2 NTCP

On the other hand, NTCP models are needed in order to make treatmentplans that either minimize the risk of developing some grade of side effect tonormal tissues for a specified dose to the target, or individualize the tumordose for an acceptable NTCP. The earliest NTCP models were based only onDVH and fractionation information, but several studies have demonstratedthe importance of considering even clinical variables such as health status,surgery, chemotherapy, base-line organ function or organ co-dependence. Inaddition, the accuracy of the model can be further increased using biologicaland imaging predictors for radiation toxicity. Eventually, organs are in gen-eral not homogeneus, so a method that relies only on single DVH parameteris unlikely to be a faithful representation of the biological structure of theorgan. [15]. Lyman-Kutcher-Burman (LKB) and relative seriality (RS) mod-els are generally the most well known and accepted methods for predicting

23

Page 26: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

toxicity in normal tissues after RT. Eventually, even more phenomenologicalmodels based on logistic regression are used.

Lyman-Kutcher-Burman (LKB) model

In 1985 Lyman argued that normal tissue complication depends upon thevolume irradiated as well as dose, and that they could be conveniently rep-resented by an error function in dose and volume. For organs that receive anuniform dose, the NTCP can be expressed by:

NTCP =1√2π

∫ t

−∞e−t

2/2dt (1.12)

t =D − TD50(V/Vref )

mTD50(V/Vref )(1.13)

TD50(1) = TD50(V/Vref )(V/Vref )n (1.14)

where the fitting parameters are:

• TD50(V/Vref) is the dose to a fraction of the reference volume Vref ofthe organ that may lead to a complication probability in the 50% ofthe population

• Vref is the reference volume, generally taken as the whole organ volume

• m is a parameter indicating the steepness of the dose-response curve

• n, is a parameter that relates the dose tolerances for the whole or partialvolume organ uniform irradiation

The last parameter indicates the volume response of the organ, the volumeeffect. Some organs can be describe by an n parameter near to 1, meaningthat they can be seriously injured even if a small part of them receive acertain dose, while other organ may be compromised when a large portionof them receive dose, and their n parameter will be close to 0. Thus, in thisframework, organs with n ∼ 1 the dose response would be correlated withthe maximum dose Dmax, while in the case of n ∼ 0 organs the mean dose

24

Page 27: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.16: A 3D surface representation of the Lyman model for complica-tion probability for uniform partial irradiation of the heart in this example,as a function of partial volume and dose. (From Lyman, J. T., Radiat. Res.,104, S13S19, 1985)

Dmean would govern the outcome. Figure 1.16 is a 3D plot representing theLKB NTCP model (Eq.1.12) for heart as a function of both the dose and thepartial volume irradiation.

Relative seriality (RS) model

In order to understand better the volume dependence of different organs todifferent organ distributions, it may be helpful to consider organs composedof smaller functional sub-units (FSUs) [18]. A serial arrangement of the FSUsmeans that the organ preserves its functionality only if all the FSUs survivethe irradiation; on the contrary, parallel architecture preserve organ func-tions unless all the FSUs are inactivated by radiation. The so-called relativeseriality model (Kallman et al. 1992) represents an attempt to construct aquasi-mechanistic model for NTCP which takes into account the architec-ture of an organ; The organ is assumed to be arranged in a combination ofparallel and series FSUs. Starting from equation1.15, derived from the linearquadratic model for cell survival after fractionated dose delivery, we obtain:

P (Dtot) = 2exp[eγ(1−Dtot/TD50)] (1.15)

where P (D) is the probability of no cell survival, Dtot is the total dose deliv-ered, TD50 is the dose causing the 50% response rate and γ is the normalized

25

Page 28: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

dose response gradient. Then Poisson statistic is used to describe the prob-ability to inactivate the organ. For an organ composed by m purely serialsub-units the probability of complication will be:

NTCP = 1−m∏i=1

(1− Pi) (1.16)

while for n purely parallel FSUs:

NTCP =n∏j=1

Pj (1.17)

and thus for an organ composed by mxn matrix of serial and parallel FSUs:

NTCP =n∏j=1

[1−

m∏i=1

(1− Pij)

](1.18)

The final expression for the RS model is obtained by introducing the param-eter s describing the relative seriality of the organ (fully parallel organ s = 0,fully serial organ s = 1) which has been demonstrated to be equal to 1/nwith n parameter of the LKB model (Eq.1.14). After some algebraic manip-ulation, it was found that for M functional volume of fractional volume ∆vithe NTCP expression is:

NTCP =

[1−

M∏i=1

[1− P (Di)s]∆vi

]1/s

(1.19)

Logistic regression

A more phenomenological approach is found in the logistic regression. Thesigmoidal relation between dose and response is suitable for a logistic regres-sion model defined as:

NTCP =1

1 + e−g(x)(1.20)

where:

g(x) = β0 +n∑i

βixi (1.21)

26

Page 29: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

with x1, x2, .., xn different input variables and β0, β1, .., βn the correspondentparameters of the regression.Logistic regression is applicable whenever the dependent variable g assumesdicotomic values, such as in the case we want to evaluate the probability todevelop or not a certain toxicity endpoint. This model is now available inmany commercial statistical package such as SPSS (statistical package forsocial science). Constructing the logistic model requires a pre-selection ofthe best combination variables, trying all the possible combination wouldbe too computational expensive in many cases and may lead to some wrongestimates. The user generally selects the variables relying on a threshold ofsignificance.

1.4 Monte Carlo beam transport simulation

In physics and also in radiotherapy applications it is often necessary to havemethods to describe problems involving large number of particles and com-plex geometries, where analytic approaches fail to be efficient. Simulationswith Monte Carlo methods are the most widespread numerical tools able todescribe these kind of phenomena. Generally the more is the complexityof the problem, the more is advantageous the use of a Monte Carlo codeas compared to analytic approaches (Fig. 1.17). Monte Carlo methods aremathematical tools to perform numerical calculation for physical and otherscientific problems. They are based on statistical sampling experiments withrandom numbers and probability distributions. Monte Carlo simulationshave been used in medical physics from the ’60 and are nowadays widespread,since the power of the new calculators allows to use this method in many sit-uations [19]. Nowadays, in both research and hospital structures there is anincreasingly adoption of Monte Carlo methods and several codes dedicatedto radiation physics are implemented (SHIELD-HIT, GEANT4, FLUKA,PHITS) in the TPS of the facilities [20], [21]. Monte Carlo simulation is par-ticularly indicated for particle transport which is a stochastic process, whereenergy, position and direction of each particle are independent random vari-ables. It is thus possible to track the particle history (i.e. the interactions)of particles traversing a medium. More in detail, a trajectory is discretizedinto small steps and the distance s (step length) between two interactions inthe medium is:

s = −λln(1− ε) (1.22)

27

Page 30: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 1.17: Pictorial representation of the differences between an analyticapproach vs a Monte Carlo method.

where λ is the mean free path which depends on the cross section σ for theinteraction and then on particle energy

λ =ρNAσ

A(1.23)

where ρ is the density of the medium, NA is the Avogadro’s number andA is the atomic mass number. while ε is a real number ranging from 0 to1. At each step the interaction characteristics are randomly sampled fromappropriate probability density functions which are derived from experimentcross section for the interaction. As long as the physic model describing theinteractions is reliable, many repeated sampling of the probability distribu-tion for a sufficient number of particles, converge to a realistic result.Monte Carlo codes in radiation research are divided in two main categories:

• Macroscopic radiation transport codes: they cover the entire irradiationvolume, but are limited in spatial and energy resolution, i.e. down to1 keV electrons (e.g. GEANT4, FLUKA, MCNP, EGS4);

• Track structures codes: they describe a small part of the track in its full

28

Page 31: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

details, thus adopting very low thresholds for both spatial end energeticresolution i.e. down to 1 eV (e.g. TRAX, OREC, PARTRAC);

1.4.1 GEANT4

Geant4 (geometry and tracking) is a software tool based on MC code for thesimulation of macroscopic radiation transport of particles traversing matter.Geant4 is completely implemented in C++ programming language and sinceits first version released in 1998 it has been continuously upgraded. Geant4covers applications in all physics areas which requires simulation particle in-teraction (e.g. astro-particle physics, nuclear physics, medical applications,radiation protection). Geant4 is able to simulate particles in the whole irra-diation taking into account also filters, scatterers, collimators, etc. (Fig. ??.Geant4 is composed by a broad collection of library classes assembled in 17major categories. For example, geometry category permits the creation ofthe volume and the coordinate system where the user intend to propagate theparticles. This volume can be composed by non-conflicting sub-volumes ofdifferent shapes and materials. Physics category instead manages the phys-ical processes involved in the simulation. Several physical models are im-plemented in Geant4 depending on energy range, particle type and medium,including physics of photons, electrons, hadrons and ions up to energies of1012 eV. For an overview of the all different categories we refer to the Geant4userguide [23].

Figure 1.18: Example of a geometry implemented in G4 [22].

29

Page 32: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Chapter 2

Material and Methods

This study is based on a set of patients treated at the proton therapy cen-ter in Trento (IT) for brain tumors. Aim of the work is to find dosimetricpredictors able to the determine the onset of toxicity events after a protontherapy treatment and to develop an NTCP model based on multivaraitelogistic regression for these endpoints. In our study the radiation induced fa-tigue (RIF) and radiation induced alopecia (RIA) endpoints were considered.Different dose metrics were extracted from the dose maps of the patients andstatistical tests were employed to find statistically significant correlations be-tween dose metrics and toxicity outcomes prior to develop the NTCP model.A subsequent study on two subsets of the initial patient set was carried outin order to account for differences in dose distributions when using the Mc-Namara [24] variable model for RBE.Therefore a description of the proton therapy facility and of the set of pa-tients considered for the analysis will be given in the first part of this chapter.Furthermore, the procedure adopted for dose metrics extraction and of thestatistical analysis employed will be presented in detail. Validation of theRBE calculation and the application of the variable RBE model to the sub-sets of patients considered will be also presented.

30

Page 33: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.1: Schematic representation of the beam line at the Trento Proton-therapy center. Starting from the left we have the cyclotron, two gantriesand the experimental room.

2.1 Materials

2.1.1 Trento proton center facility

The patient database analyzed in this work was produced at the proton ther-apy facility of Trento (I), which is one of the three hadron therapy structuresactually available in Italy, together with the CNAO center in Pavia and theCATANA center in Catania. Trento started the activity in October 2014,and, up to now has treated about 300 patients [2]. The center was bornin collaboration with AtreP (Agenzia Provinciale per la Protonterapia) andwas constructed by IBA (Ion beam applications) company and it is now partof the Trentino healthcare agency APSS (Azienda Provinciale per i ServiziSanitari). The structure (Fig.2.1) relies on a cyclotron able to accelerateprotons up to about 230 MeV, and distribute them with the beam line to thetwo gantries where patients are treated, or to the experimental room, whereexperiments are mainly conducted in collaboration with TIFPA (Trento In-stitute for Fundamental Physics and Applications) which is a part of theINFN (Istituto Nazionale di Fisica Nucleare).

Beam line

The accelerator used in the Trento facility is an isochronous cyclotron pro-duced by IBA (ion beam applications), able to accelerate protons up to an

31

Page 34: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.2: Left: IBA 230 MeV cyclotron installed in Trento. The magnethas a diameter of 4.34 m and it is 2.1 m high. Right: Scheme of a cyclotron

energy of about 230 MeV. A cyclotron is called isochronus if it keeps the sameorbital period independently on the energy and radius of the particles, thusa single RF is needed during the acceleration process. The cyclotron is com-posed by a proton source located at the center, a radiofrequency RF electricfield orthogonal to a strong magnetic field produced by a magnet (Fig.2.2).Protons produced by the source are accelerated in the gap between the deesby an RF electric field, then they cross a region were a constant magneticfield curves their trajectory thanks to the Lorentz force, ~F = q~v ∧ ~B. Theparticle velocity increases at each transition between the plates thanks to thepotential difference applied and the radius of curvature R increases as well,since it is proportional to the particle velocity (R = mv

qB). When the protons

reach the maximum energy, an extraction system collects the particles andguide them into the beam line. In order to achieve the energies used fortherapeutic purposes (70 to 230 MeV), an energy selection system (ESS) isincluded into the beam line. ESS is composed by a proton degrader followedby a beam analyzer to select the energy and energy spread of the beam. In theproton degrader we have beam attenuation and spread, thanks to a degradermaterial. In order to set the outgoing energy, the material thickness mustbe adjusted and a carbon wedge, ”rolled up” along the surface of a wheel, isused to this purpose. The degrader can have two functions. Firstly, it canbe used as a range shifter to set the maximum needed energy in a certaintreatment field, where the energy modulation is performed in the treatmentnozzle just before the patient. Secondly, it can be used directly as an energymodulator, which then requires a fast response of the magnets [25]. Figure2.3 shows a the degrader unit and an example of a degraded beam spectrum

32

Page 35: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.3: Left: degrader unit, with the red arrow indicating the protonbeam direction [25]. Right: the momentum spectrum of 250MeV protonsdegraded to 230, 172, 100 and 75MeV. The vertical dashed window indicatesthe typically selected momentum spread of ±0.5% [26].

acquired at the proton therapy facility at the Center of Proton Therapy ofthe Paul Scherrer Institute (PSI) [26].The momentum selection is performed by a beam analyzer behind the de-

grader composed by two large dipoles bending the beam around 45◦. Thebeam optics is designed to have a dispersive focus halfway between the bend-ing magnets. At this location a slit system select the energy and energyspread that are accepted for the treatment. Eventually the second bendingmagnet compensate for the dispersion and makes the beam independent onthe beam energy. After the ESS the beam line divides into three paths, onefor each treatment room (gantries) and one for the experimental room. Forthe two gantries the beam reaches the nozzle composed by two fast scan-ning magnets able to scan the xy-plane orthogonal to the beam direction z(Fig.2.1.1).

Scanning technique

The technique used in Trento for shaping the dose distribution is the pencilbeam scanning (PBS), which is currently the most flexible available solution.Compared to a passive scattering technique, the pencil beam scanning allows

33

Page 36: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.4: Scheme of the nozzle. a) beam being bent by the 135◦ magnet inthe gantry; b) movable ionization chamber (IC) to check beam properties; c) 2quadrupoles to focus the beam at the isocenter; d) 2 fast scanning magnets; e)movable x-ray tube to allow beam eye view x-ray shots; f) vacuum chamber;g) set of ICs; h) drawer to install range shifter

a better covering of the tumor volume (Fig.2.5) and a better modulation ofthe intensity. Dose delivery is achieved by two fast scanning magnets inthe nozzle, that must yield a velocity for the pencil beam displacement of1cm/ms. Fast magnets scan in the plan orthogonal to the beam direction,while scanning in depth is achieved by ESS described above. For shallowseated tumors (i.e. depth lower than 4.1 cm), an additional range shifter canbe installed right before the nozzle exit at different distances from it.

2.1.2 Patients and outcome

In this study a set of 85 patients undergoing proton therapy (PT) for braintumor (BT) was considered. Patients were treated in the Trento protoncenter facility between 2015 and 2017. Patient median age was 55 years(range 30 to 84 years) and their median follow up was 5 months (range 1to 19 months). The technique used for the irradiation was the pencil beamscanning (PBS), releasing the prescription dose D to the tumor (D rangingfrom 20-72 Gy) in fractions d = 1.8−2.2 Gy, for a number of fractions n from12 to 36. Patient related characteristics such as age, gender, chemotherapy(CHT), re-irradiation, were taken into account in the analysis. The RTplans generated following dose prescriptions with the Raystation v.6 software[27] used at the Trento proton therapy center, were available for exporting.

34

Page 37: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.5: Comparison of the dose distributions for a scattered beam (thelight curve represents the 95% isodose line) and one obtained with pencilbeam scanning

Furthermore, clinical data and toxicity events observed during the follow-upwere scored and organized by clinicians in the clinical Mosaiq database ofthe facility. We considered Radiation induced fatigue (RIF) and radiationinduced alopecia (RIA) as endpoints for the analysis. Both RIF and RIAwere previously scored according to the CTCAE v.4 (common terminologycriteria for adverse events) scoring system. RIF was scored from grade 0 to3 while RIA from grade 0 to 2. Figure 2.6 reports description of the scoringused in accordance with the CTCAE. We separated toxicity outcome in acuteand late events. An acute events occurs within 90 days after the end of thetreatment, while an event is classified to be late if it occurs after 90 days fromthe end of the treatment. The analysis of late events is in general of greatinterest, since it is related to a non-temporary toxicity, which may becomeeven permanent. Skin was not considered an OAR in the plan and no doseboundary were imposed to this structure, while for brainstem standard dosesboundary were adopted.

2.2 Method

2.2.1 Dose metrics extraction

The dicom CT, RT structures and RT doses were firstly exported fromRaystation and they were converted using CERR (computational environ-ment for radiotherapy research) software into MatLab readable format (Math-

35

Page 38: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.6: CTCAE v.4.03 scoring system for fatigue and alopecia [28].

Works, Natick, MA, USA). CERR is an open source, freely available generaltreatment plan analysis package based on MatLab. CERR capabilities forradiotherapy treatment response modeling include the ability to import fulltreatment planning data sets from treatment planning systems, a convenientgraphycal review of the data, manipulation of the structures and ability toderive dose-volume histograms (DVH) and dose surface histograms (DSH)[29]. Brain stem maximum dose, mean dose and the Vx points of the DVHswere extracted for the fatigue analysis. In the analysis of the RIA skin max-imum dose, mean dose and Sx points of the DSHs were extracted. Vx and Sxare the volumes and the surface of the considered organs receiving at least xGy of dose, respectively. Both Vx and Sx were extracted in steps of 5 Gy.

DVH and DSH

Dose volume histograms are often considered in literature as representative ofan organ irradiation and then they are considered in development of NTCPmodel (e.g. LKB model, sec.1.3). DVH condenses the complex 3D dosepattern on the organ considered to a one dimensional curve, where each ofits points Vx is the volume of the organ that receives at least x Gy of dose.This approach of course reduces the complexity of the analysis, but leaks ofrepresentative power in case of not homogeneous irradiation. On the otherhand dose surface histograms (DSH) extracted in the analysis of the RIA,were considered to be representative of the irradiation of thin cutaneous layerof the scalp. These histograms have the same meaning of the dose volumehistograms described above, with the difference that we are now consideringthe organ surface instead of volume. This choice is particularly indicated

36

Page 39: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.7: A pictorial representation of the Body dose-surface histogramextraction from the external body shell dose-volume histogram [30]

in this case where the organ to be investigated is the skin, which is bestmodeled by a surface than a volume. This procedure was first adopted in2016 (Pastore et al.[30]) in evaluating the risk of severe acute skin toxicity inbreast cancer patient. To calculate absolute DSH, they extracted the relativecomplement in the skin contouring structure (body) of its 3D erosion definedby a spherical structuring element of radius r ∼ 3mm (i.e. the order ofmagnitude of mean skin thickness). On such shell, the absolute dose-volumehistogram was regularly computed and then divided by r to obtain the DSH(Fig. 2.7).In the same way we extracted the DSH, starting from the body structureof the scalp and taking the complement of its 3D eroded structure, withspherical structural element r of 4 mm, mean depth of human hair follicle,which is considered to be the sensible target for RIA. An example of a patientfrom our set is shown in figure (2.8). DVH and DSH were then normalized inorder to be independent on the individual characteristic. DVH for brain stemand HCT were normalized with the total volume of their respective structure.Relative DSH were instead obtained normalizing the absolute DSH with thesurface of the healthy cerebral tissue (HCT). The reason for this choice reliesin the fact that the skin of the scalp is not a well defined organ in this context,

37

Page 40: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.8: Example of a patient of the set considered in this work. Right:a transversal slice taken from Raystation v.6 representing the body structurein blue and the RT dose. Left: absolute DSH of the same patient.

so we considered an organ, with a smaller surface, but that scales similarlyto the skin in the scalp region. This may lead to Sx > 1, but it should notrepresent a problem if we know how the relative DSH has been built.

2.2.2 Statistical analysis and NTCP model

The statistical analysis was developed in collaboration with the IBB (In-stitute of Biostructure and Bioimaging) of the CNR (Consiglio NazionaleRicerche) of Naples (IT). SPSS (statistical package for social science) com-mercial software was employed for statistical analysis.Chi-squared test and Mann-Whitney test were employed for univariate sta-tistical analysis. Chi-square tests were performed in order to determine ifthere are significant relations between patient and treatment-related charac-teristics (age, gender, CHT, re-irradiation), and toxicity outcomes.Chi-square tests are statistical hypothesis tests where the sampling distribu-tion of the test statistic is a chi-squared distribution when the null hypothesisis true. The chi-squared test is generally used to determine whether thereis a significant difference between the expected frequencies and the observedfrequencies of one or more categories. For a sample with k possible events,

38

Page 41: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

the chi-square variable is:

χ2 =k∑i=1

(oi − ei)2

ei(2.1)

where oi are the observed frequencies, while ei the expected ones. Once thevalue of χ2 is known, tables of significance lead us to the eventual rejectionof the null hypothesis, for a choice of the significance value. The significancethreshold for the test was set to p = 0.05.

Mann-Whitney U -tests were employed to evaluate if there is a statisticalsignificance that dose metrics are differently distributed among two sam-ples of the patient population based on the outcome. Mann-Whitney U -testis a non parametric statistical test for independent continuous data. Nonparametric statistical analysis is adopted in cases where the variable is notdistributed normally. For normally distributed variables Mann-Whitney testis substituted by the parametric Student t-test. A normality test was thusperformed before the test analysis. Assumptions of the Mann-Whitney U -test are:

• the two samples under study have to be reciprocally independent andeach observation inside the sample is independent from the others;

• the observations can be compared;

the U -test calculates the ranks of the whole population, then divide the pop-ulation in 2 subsets, based on the outcome. Thus a statistic U is calculatedfor each subset as U = R − n(n+1)

2, where R is the rank sum of the subset

and n the number of observations for the subset. Eventually the lower valueof U is used when looking to the significance tables.U -test highlights possible dosimetric variables that correlate with a certainoutcome. The p-value was set to p = 0.05 also in this case.In our case population is divided in 2 sub-population discriminated by a di-chotomous variable relative to the grade of fatigue or alopecia developed bythe patients (e.g. 1 if patient developed alopecia, 0 if not). Then the testsestablishes if some of the dose metric extracted or clinical variables correlateswith the outcome.

39

Page 42: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.9: ROC curve explanation for a random guess: as the AUC ROCapproaches 1, the model increases its predictive power. Blue points representpossible (FP, TP) rate couples in the ROC space.

In case we found statistically significant variables we proceed in developingan NTCP model based on a multivariate logistic regression, described inSect. 1.3. Logistic regression model, being a phenomenological model, ismore versatile than LKB or RS models, which generally require a larger setof data to be accurate. Again the SPSS software was employed for the modelcomputation.Model performance was measured by the area under the ROC curve (AUC-ROC). The ROC (receiver operating curve) is a graphical scheme used indecision theory to describe the predictive power of a model (Fig.2.9). On they-axis it represents the probability of having a true positive (TP) outcomefrom the model, also called sensitivity, while, on the x -axis the probabil-ity that the model returns a false positive (FP), also called 1− specificity.Therefore the points of the ROC curve are the couple (FP, TP) rates forthe data under study when varying a classifying parameter. The AUC-ROCparameter describes the predictive power of the model, which increases as

40

Page 43: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.10: Scheme of the procedure adopted for statistical analysis.

the AUC-ROC approaches 1. The Youden’s J index was calculated. Theindex was suggested by W.J. Youden in 1950 [31] as a way of summarizingthe performance of a diagnostic test. Its value ranges from -1 to 1, and hasa zero value when a diagnostic test gives the same proportion of positiveresults for groups with and without the disease, i.e the test is useless. It isdefined for each point of the ROC as:

J = sensitivity + specificity− 1 (2.2)

The maximum value of the index may be used as a criterion for selecting theoptimum cut-off point when a diagnostic test gives a numeric rather than adichotomous result.A schematic summary of the procedure described above is depicted in Fig.2.10.

2.2.3 RBE weighted dose maps recalculation

Recently the proton therapy center of Trento obtained the released researchversion of Raystation v.7, which performs calculations of dose averaged LET(LETd) maps from treatment plans, thanks to a Monte Carlo internal mod-ule which simulates the particle transport.When we deal with monochromatic beams, the LET calculation is easilyachieved because the kinetic energy is well defined. On the contrary, clinical

41

Page 44: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

beams are not mono-energetic and possess a kinetic spectrum at a certaindepth. Therefore is more meaningful to introduce the concept of LET dis-tribution and hence, to deal with mean LET value. LETd is thus defined as[32]:

LETjd =

∫∞0S

2jel (E)ψjE(z)dE∫∞

0ψjE(z)dE

(2.3)

where ψ is the energy spectrum of the particles at depth z. LETd mapscan be employed to calculate maps of variable RBE and thus new RBEweighted dose maps. Several variable RBE models are found in literature(e.g. LEM, Wedenberg, McNamara, Carabe) and going into the details ofall is beyond the scope of this work. However it is worth to say that RBEmodels can be in general based on the full spectrum of particles and energiespartecipating in to the irradiation. They are based on radial dose distributionof ions traversing the medium and they consider the local damage inducedby these ions (LEM [33], MKM [34]). On the other hand, simplier analyticalapproaches rely only on macroscopic quantities, such as LETd and Dose D,obtaing their analytical equation by fitting experimental data (McNamara[24], Wedenberg [35], Carabe [36]) damage that each particle can The modelwe rely on the one introduced by McNamara.

Figure 2.11: The RBE for cell survival as a function of LETx and (α/β)x fora dose of 2 Gy (left panel) and 8 Gy (right panel) [24].

42

Page 45: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

McNamara model

The McNamara variable model of RBE is based on experimental data of 76studies for a total of 369 data points, presented in Paganetti (2014) [13].These data were extracted and analyzed in the framework of the linear-quadratic (LQ) model, in order to parameterize the dependence of the RBEon the LETd and (α/β)x for proton therapy. For each experimental data setthe following parameters were extracted: αx, βx and α, β, to describe thetissue response to photon radiation and proton radiation respectively andLETd at the position of the biological sample. McNamara restricted the val-ues to be taken into account to LETd < 20 keV/µm and (α/β)x < 30 Gy inthe fit. This restriction is intended to collect only the data which fall intothe clinical relevant LETd range, where the relation between RBE and LETd

may be approximately linear.

RBE[Dp,

(αβ

)x, LETd

]=

1

2Dp·

[((αβ

)2

x+ 4Dp

(αβ

)x

(0.999064 +

0.35605

(α/β)LET

)+

+4D2p

(1.1012− 0.0038703

√(α

β

)x

LETd

)2) 1

2

−(αβ

)x

](2.4)

The formulation given in equation 2.4 depends on the proton dose Dp, theratio (α/β)x and the dose averaged linear energy transfer (LETd). Depen-dence of the RBE for cell survival on LETd and (α/β)x is shown in Fig.2.11for Dp of 2 Gy and 8 Gy as predicted by the model. The RBE is expectedto increase as the LETd increase and as the (α/β)x decreases in accordancewith the biological model described in Sec.1.2.2. Dependence of the RBEon the Dose Dp is shown in Fig. 2.2.3, for different (α/β)x ratios and LETd

= 2.5 KeV/µm. The RBE decreases with increasing dose for (α/β)x ≤ 2Gy and approaches 1 for high doses. For large (α/β)x values, the slope theMcNamara model converges to zero with RBE ∼ 1.08 and 1.05 for (α/β)x =10 and 15 Gy, respectively. Other similar radiobiological models are found inliterature: Carabe et al. model [36] and Wedenberg et al. model [35] whichare both based on a smaller set of data compared to the model described sofar. A comparison between models is found in Fig.2.13 and in Fig. 2.2.3,where we notice a good agreement between McNamara et al. model and

43

Page 46: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.12: The RBE as a function of dose for different (α/β)x values. Threedifferent models predict the RBE: McNamara et al. model (blue solid line),the Carabe et al. model (green dashed line) and the Wedenberg et al. model(pink dotted line). Adapted from [24].

44

Page 47: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Wedenberg et al. model for low Dp, in particular for low LETd values.

Figure 2.13: RBE for cell survival as a function of α/β for different LETdvalues and a dose of 2 Gy. Three different models predict the RBE: ourmodel (blue solid line), the Carabe et al model (green dashed line) and theWedenberg et al model (pink dotted line). Adapted from [24]

LETd validation

LETd calculation is not a trivial task and rely on a Monte Carlo computationwhich simulates the components of the irradiation field and the geometry ofthe system. Therefore, Raystation LETd calculation was firstly compared toa Monte Carlo simulation performed by Geant4 to validate it. The valida-tion was performed in a simulated water box phantom of 15x15x15 cm3, voxelsize was set to 0.1 cm. A beam of E = 120 MeV and ∆E = 0.8 MeV waschosen for the comparison. Raystation simulated 109 protons, while withGeant4 we are able to simulate 106 protons otherwise it would have beencomputationally too expensive. For the simulation in Geant4 we adoptedthe Hadrontherapy class developed by the LNS (Laboratori Nazionali delSud) group of INFN [37]. Dose maps were firstly compared for the spatial

45

Page 48: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

distribution and the IDD (integrated depth dose) curve along the beam di-rection. Since the doses of Raystation and Geant4 are clearly different due tothe different statistics, they were properly normalized with respect to theirmaximum. After that LETd spatial distribution maps were compared be-tween Raystation and Geant4 simulations. Employing LETd distributions,RBE maps were then computed following the McNamara model for physicaldoses of 1 Gy and α/β = 2 in order to highlight discrepancies (Fig. 2.11).RBE weighted doses were finally calculated and their IDD curves were com-pared.

Application to a patient subset

We considered two subsets of 10 patients, one for RIF and one for RIA. Pa-tients for RIF were selected among the patients with D > 0 to the brainstem,differently the patients for RIA were chosen between the patients having thehigher RS20Gy in order to highlight the differences in dose maps. The calcu-lation of the new dose maps relies on dose averaged LET (LETd), α/β valueand on spatial physical dose distributions. Dose distribution were alreadyextracted for the first part of the work. LETd maps were instead calculatedusing the new research version of Raystation v.7. A Raystation script basedon Python language was then developed in order to calculate the RBE mapsand the RBE weighted dose maps directly on Raystation, avoiding subse-quent exporting and importing of patient plans from Raystation to othersoftwares. A recent work reports α/β = 2.5Gy for the brainstem structure[? ], while it is not uniquely reported in literature a clear indication for thevalue of α/β for the body structure we have considered for RIA. Thereforewe conducted a sensitivity analysis varying α/β from 2 to 10 Gy, which aregenerally the most extreme cases. The procedure is depicted in Fig.2.14.

From the new dose maps DVH and DSH metrics were extracted withthe same procedure described in described in Sec. 2.2.1. Then, mean DVHand mean DSH were compared for different α/β values. Finally WincoxonW-test were employed for the 10 patients in order to search for statisticallysignificant differences between the metrics extracted. Wilcoxon W-test isa non parametric statistical test for paired data. It is the statistical testcorresponding to the Mann-Whitney U-test described in Sec. 2.2.2 for nonindependent data. In this case the data were paired since we were looking fordifferences in dose metrics extracted from different dose maps belonging to

46

Page 49: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 2.14: Procedure steps from the left to the right: starting from theoriginal plan, we calculate the LETd map, from which we derive the RBEmaps for different α/β ratios. Finally we calculate the new RBE weighteddose maps.

the same patients. The p-value chosen as the significance level was p = 0.05.

47

Page 50: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Chapter 3

Results and discussion

This chapter presents and discusses the results of the work. First part willbe dedicated to the statistical analysis outcomes, concerning RIF and RIA,and the NTCP model for RIA derived from multivariate logistic regression.Secondly, results concerning the application of the McNamara model of RBEon dose maps will be presented, focusing firstly on the validation of the LETd

calculation of Raystation and then on the application of the model in recal-culating dose maps of brainstem and body structures on two subsets of 10selected patients.

3.1 Statistical analysis

3.1.1 RIF and RIA Outcomes

Outcomes for RIF and RIA are reported in table 3.1. We divided the variousgrades in dichotomous outcomes (i.e. 1 for grade ≥ G1 and 0 otherwise, or 1

Outcome RIF RIA≥G1 Acute 69 of 83 (83%) 47 of 78 (60%)≥G2 Acute 1 of 83 (< 2%) 38 of 78 (49%)≥G1 Late 29 of 62 (47%) 32 of 59 (54%)≥G2 Late 2 of 62 (< 4%) 19 of 59 (33%)

Table 3.1: Acute and late outcomes for RIF and RIA.

48

Page 51: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

V10 V15 V20 V25 V30 V35 V40 V45 V50Acute 0.728 0.432 0.349 0.154 0.265 0.254 0.304 0.334 0.352Late 0.901 0.918 0.930 0.971 0.928 0.982 0.994 0.939 0.900

Table 3.2: p-values for differences between mean Vx points between patientsdeveloping or not acute or late G1 RIF

for grade ≥ G2 and 0 otherwise. According to the CTCAEv.4 classification(Fig.2.6), we notice that the great majority of the toxicity events associatedto fatigue, for both acute and late events, are grade 1 (G1) toxicities. Moresevere grade of RIF are found in very few patients, in particular, the mostsevere grade 3 is not even present. On the contrary, alopecia events are moresevere. Maximum grade 2 of RIA is present with a substantial percentage inboth acute and late analysis. Acute G1 RIF was observed at a median timetm = 38 days after the end of PT (6-84 days), while late G1 RIF at a tm= 114.5 days (91-497 days). Acute G2 2 RIA was found at a tm = 37 daysafter the end of the treatment (range 6 to 58 days), while Late Grade 2 RIAwas found at a tm of 112 days (91 to 264 days).

3.1.2 RIF analysis

No clinical variable considered is associated with acute or late G1 gradeof RIF. Neither Dmean nor Dmax correlate with the outcome. Mean DVHcomparison for the brainstem structure between patient developing or notG1 RIF is reported in Fig. 3.1. DVH comparison shows a shift of the meanDVH points towards higher values for patients developing acute RIF, whichis not present for patients developing late RIF. Nevertheless, the shift wasnot found to be significant at the univariate statistical analysis. P-valuesfor acute G1 RIF are reported in table 3.2. Since results show no clinicalor dosimetric variables significantly associated with the outcome, we didnot proceed to the multivariate statistical analysis for RIF. This result is incontrast with results of similar studies with photons which report significantincrease in Dmean or Dmax to the brainstem in patients developing RIF ([38],[39])

49

Page 52: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.1: Top: brainstem mean DVH comparison between patients whodeveloped G1 or G2 acute RIF vs. those who did not. Dashed lines representstandard deviations σ of the distribution of the Vx points of the patient’sdata set. Bottom: same comparison in the case of late RIF events.

50

Page 53: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.2: Whisker box plot for the age distribution for patients developing(1) or not (0) acute G2 RIA. Box represents 25 and 75 percentiles, with themedian in the middle of the box, while the bar represent the full range.

3.1.3 RIA analysis

Clinical variables significantly associated with acute G2 RIA were CHT (p =0.01) and age (p = 0.02). Age association with the acute outcome is depictedin Fig 3.1.3. We notice that younger age is more probable to determinethe onset of G2 RIA in the acute phase. Furthermore, clinical variablessignificantly associated with late G2 RIA were CHT (p = 0.04) and acuteG2 RIA (p < 0.0001), the latter meaning that a certain persistence of toxicityexist from the acute to the late phase.Both Dmean Dmax metrics are significantly associated with the G2 outcome

in both acute and late phase (p < 0.001). Fig. 3.1.3 shows the comparisonbetween mean DSH for the body structure for patients developing or notacute or late G2 RIA. We notice that in both acute and late phase, meanDSHs are well separated, also considering standard deviations σ of the Sxdistributions. P-values relative to the Sx points of the DVH are reported inTable 3.3.It turns out that all the dose metrics extracted from the DSHs (Sx ,Dmean,Dmax) are significantly associated (p < 0.001) with the onset of both acute

51

Page 54: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.3: Top: body mean DSH comparison between patients who devel-oped acute G2 RIA vs. those who did not. dashed lines represent standarddeviations σ of the distribution of the Sx points of the patient’s data set.Bottom: same comparison in the case of late RIA events.

52

Page 55: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

S10 S15 S20 S25 S30 S35 S40 S45 S50Acute <.001 <.001 <.001 <.001 <.001 <.001 <.001 <.001 <.001Late <.001 <.001 <.001 <.001 <.001 <.001 <.001 <.001 <.001

Table 3.3: p-values for differences between mean Sx points between patientsdeveloping or not acute or late G2 RIA

and late G2 RIA. Hence we proceeded to the multivariate analysis for theseendpoints.

NTCP model for acute RIA

In the acute phase, at the multivariate analysis, age, CHT, clinical variablesand Dmax metric remain significant within the NTCP model. Dmax distribu-tion of the two populations of patients are reported in Fig. 3.4.Multivariate logistic regression parameters are reported in in table 3.4.Odds Ratios represents the exponentiation of the coefficients βi in the eq.1.21. Area under the ROC curve (AUC-ROC) was used to measure modelperformance, giving: AUC-ROC = 0.878 ± 0.038. Furthermore Youden in-dex was measured to find the optimal cut-off for determining the onset ofacute G2 RIA and results: J = 45 Gy. ROC curve for the NTCP modeldescribed above is shown in Fig. 3.5.The model has good prediction performance (AUC > 0.8) in predicting theonset of severe alopecia (G2) induced by radiation in our patient database.Dmax, the dosimetric predicting variable of the model, suggests a serial be-havior of the skin in the scalp region. This is in contrast with more parallelbehavior found in study for acute skin toxicity in patients treated with pho-tons. ([30]). Further studies are needed to determine whether the injury islocal or not to.

Odds ratio 95% CIDmax 1.112 1.050-1.178Age 0.952 0.910-0.996CHT 0.213 0.050-0.910

Constant 0.398

Table 3.4: Logistic regression G2 RIA acute

53

Page 56: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.4: Whisker box plot for the Dmean distribution for patients develop-ing (1) or not (0) acute G2 RIA. Box represents 25 and 75 percentiles, withthe median in the middle of the box.

Figure 3.5: ROC curve of NTCP model derived for acute G2 RIA

54

Page 57: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

NTCP model for late RIA

Concerning the toxicity in the late phase, at the multivariate analysis, onlyS20 remains significant within the NTCP model. SPSS returns for logisticregression NTCP model the following parameters: Odds Ratio= 1.163, 95%CI 1.071-1.262; constant= 2.352. Representation of the model is shown inFig. 3.6. We can there notice the typical sigmoidal shape of the NTCPmodels described in Sect. 1.3 .Area under the ROC curve to measure model performance results AUC-ROC= 0.893 ± 0.041. ROC curve is shown in Fig. 3.7. Youden J-index establishesthe optimum cut-off for determining the onset of late G2 RIA to S20 = 9.9%.The model we obtained has good prediction performance in determining theonset of grade 2 radiation induced alopecia. Nevertheless, the possibility toextend the database of patients may lead to a more robust NTCP model andmake it suitable for a comparison with different models (e.g. LKB).

Figure 3.6: Representation of the NTCP model derived from multivariatelogistic regression for late G2 RIA. Red points represent S20 for patient withoutcome 1 for late G2 RIA. Blue points are S20 of patients with outcome 0.

55

Page 58: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.7: ROC curve of NTCP model derived for late G2 RIA.

56

Page 59: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.8: Dose simulation. Left: Raystation. Right: Geant4

3.2 RBE maps

3.2.1 LET validation

Dose calculated with Raystation and Geant4 shows good agreement for spa-tial distribution (Fig. 3.8, 3.9). Curves shown in Fig. 3.9, are two orthogonalprofiles of the bragg peak, and they are similarly distributed. We impute thedifferences to the lower statistic of the Geant4 simulation compared to theone of Raystation.

Figure 3.9: comparison of bragg peak dose profiles on directions orthogonalto the beam direction between Raystation and Geant4.

57

Page 60: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.10: Comparison of IDD curves between Raystation and Geant4.

Also idd curves along the beam direction are reported, normalized withrespect to their maximum, and show a very good agreement (Fig. 3.10).On the other hand, when looking at the LETd distributions we find a dis-

crepancy between Raystation and Geant4 simulations. Fig. 3.11 and 3.12shows the spatial distribution of the LETd for Raystation and Geant4. Wenotice that spatial distribution of Geant4 is wider in the entrance channel.Furthermore, Raystation simulates a uniform arched distribution, which isnot present in Geant4. We impute this behavior to the different modelsadopted by the two Monte Carlo codes for particle tracking, in particularin cut’s thresholds for electromagnetic nuclear interactions, rather than tothe different statistics of the simulations. This because, even with lowerstatistics, Geant4 simulates particles in regions not populated by Raystationsimulation. This is clearly visible yet in the entrance channel and also inthe lateral spread at the Bragg peak depth (Fig. 3.11). Missing statisticsdoes not seem to contribute to fill a sharp arched front as in Raystation, butrather to fill a more flat front. Furthermore, transverse cuts of Fig. 3.12.Despite the different spatial distribution of the LETd, dose maps, show verygood agreement. This because the LETd is not weighted for the dose, in fact,regions showing major discrepancies in LETd, are populated by few particles,resulting in a negligible dose.

58

Page 61: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.11: LETd distributions over a central plane parallel to the beamdirection.

Figure 3.12: LETd distributions over transverse planes at different depths.

59

Page 62: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

In order to remove the dependence on different spatial distributions we cal-culated at each depth an average LETd value over the plan orthogonal tothe beam direction at that depth in analogy to a planar dose integration(PDD-IDD). It is important to note that, the non additivity of the LETd

would make a standard IDD curve for the LET senseless. Therefore, callingP (z) the plans at different depths, the averaged LETd is calculated as anadditional dose average, i.e.:

< LETd(z) >=

∑i∈P (z) LETi

d ·Di∑i∈P (z) Di

(3.1)

Where i is the voxel indices belonging to the plane P, while LETid and Di

are the LETd and physical dose in the voxel i, respectively. Therefore a LETi

value at each depth is obtained, which condenses the 3-dimensional informa-tion on the spatial distribution on a mono-dimensional curve. Fig.3.13 showsquite good agreement between the two simulations, even though Raystationcurve results ∼8% higher in the peak region.

Differences in LETd maps are reflected in the RBE weighted dose (DRBE)maps calculated with the McNamara model. Here IDD calculations with

Figure 3.13: LETd avaraged over plans orthogonal to the beam direction forRaystation and Geant4 simulations.

60

Page 63: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.14: RBE weighted dose maps calculated from Raystation andGeant4 simulations of LETd. Parameters: Dp = 1Gy, α/β=2Gy.

α/β = 2 are shown (Fig. 3.14). Physical doses Dp are peaked at 1 Gy. Cal-culation of DRBE relative to Geant4 simulation shows a peak ∼10% highercompared to Raystation.Even if we expect the RBE in the McNamara model to increase monoton-ically with LETd from Sec. 2.2.3, and hence the DRBE for Raystation tobe slightly higher than the Geant4 one, here it the opposite happens. Weattribute this to the more flat distribution at the peak position resulting inGeant4. Therefore, although Raystation presents on average slightly higherLETd values and hence RBE values, the integration of the IDD favors theGeant4 simulation at the Bragg peak depth. Furthermore, the α/β = 2Gyadopted maximizes the differences between the two DRBE, since the RBEhas a more steep response to LET variation for low α/β values (Fig. 2.11).It is worth noticing that in clinical practice, a combination of several quasimono-energetic beams, weighted in intensity, are adopted to build the SOBP.A comparison on a SOBP would tell us if these discrepancies are somehowcompensated and leveled out. We point out that a simulation of a SOBPis an challenging task to achieve and requires non trivial implementation inGeant4. Nevertheless, the calculation of RBE we rely on seems to be reason-able, also considering that in experiments, biological variability of samplesleads to uncertainties larger than 10%.

61

Page 64: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.15: Procedure steps: starting from the original plan (a), we calculatethe LETd map (b) from which we derive the RBE maps. Finally we calculatethe new RBE weighted dose maps (c) and then analyze the differences in thenew dose map with respect to the initial one (d).

3.2.2 Application to a patient subset

We then apply the McNamara model to two subsets of 10 patients fromthe initial database. Starting from the original treatment plan we assessfirst the LETd maps. Then we calculate compute RBE maps thanks towhich we calculate new RBE weighted dose maps. Fig. 3.15 is a pictorialrepresentation of the procedure on one patient of the database.

Brainstem

We recalculated the RBE dose maps on the brainstem with the McNamaramodel on a sub population of 10 patients receiving non-zero dose to thatstructure. We considered α/β parameter equal to 2 and 10 Gy. Mean DVHsare compared in Fig. 3.16. We notice a clear shift towards higher Vx pointsfor low (α/β)x = 2, in particular Dmax increases of more than 10%, while for(α/β)x = 10 the Vx differences are shallower to the dose map with RBE =1.1. Nonetheless, differences are found to be significant for several of the Vxpoints. Wilcoxon W-test for paired data shown in Fig. 3.17 and Fig. 3.18,reports the p-values relative to the Vx points extracted.Results of the W-test imply the need to extend the recalculation to the whole

initial set of patients, in order to see whether a shift to Vx points may lead tovariation in the univariate statistical analysis previously performed for RIF.Brainstem is an interesting structure for RBE weighted dose recalculation,since, due its deep position, it is often subject to the distal part of the beams,

62

Page 65: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.16: Mean DVHs of the brainstem for 10 patients. Comparisonbetween dose maps recalculated with McNamara RBE model for (α/β)x = 2and 10 Gy, compared with the original map with RBE = 1.1.

Figure 3.17: Wilcoxon W-test between Vx of the brainstem extracted fromdose maps calculated with (α/β)x = 2 and constant RBE = 1.1

63

Page 66: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.18: Wilcoxon W-test between Vx of the brainstem extracted fromdose maps calculated with (α/β)x = 10 and constant RBE = 1.1

characterized by high LET values and hence steeper gradients RBE valuesand thus RBE weighted dose, according to the model adopted. Thereforedifferences between constant or variable model of RBE are maximized forthis structure.

Body

The procedure described above for brainstem was applied also for the bodystructure to other 10 patients selected among the patients with higher valuesof S20 from the initial database. Mean DSH comparison is reported in Fig.3.19. We notice a shift towards higher Sx values and an increase of Dmax

of ∼ 10% for (α/β)x = 2. On the contrary, mean DSH of (α/β)x = 10shows a slight shift towards lower Sx values. Wilcoxon W-test returns signif-icant differences in several Sx values between original dose maps and thoserecalculated with (α/β)x = 2 or (α/β)x = 10 (Fig. 3.20, Fig. 3.21).

Also in this case, the result of the W-test suggests the need to extend theRBE recalculation to the whole database of patients. A significant increaseof the DSH point may lead to variations in the statistical analysis previouslyperformed and thus on the parameters of the NTCP model derived fromlogistic regression.

64

Page 67: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.19: mean DVHs of the body structure for 10 patients. Comparisonbetween dose maps recalculated with McNamara RBE model for (α/β)x = 2and 10 Gy, compared with the original map with RBE = 1.1.

Figure 3.20: Wilcoxon W-test between Sx of the body structure extractedfrom dose maps calculated with (α/β)x = 2 and constant RBE = 1.1

65

Page 68: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Figure 3.21: Wilcoxon W-test between Sx of the body structure extractedfrom dose maps calculated with (α/β)x = 10 and constant RBE = 1.1

66

Page 69: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Chapter 4

Conclusions

A set of 85 consecutive brain tumor patients treated in the Trento protontherapy center for brain tumor was analyzed in a retrospective analysis. Weassessed acute (≤ 90 days) and late (> 90 days) toxicity events concerningradiation induced fatigue and radiation induced alopecia. We considered clin-ical variables and treatment related characteristics such age, gender, CHT,re-irradiation, and we extracted DVH and DSH dose metrics for brainstemand body structure respectively, in addition to Dmax, Dmean metrics.Analysis of RIF does not show any significant association between variablesconsidered and toxicity outcomes. It is worth noticing that scoring of RIFrecords almost only G1 toxicity in both acute and late phase, in contrastwith other works reporting most severe outcomes. Further work is thusneeded to understand whether patients may benefit from therapy with pro-tons compared to photons concerning fatigue outcome. Therefore, assessingdata coming from a different cohort of patients treated with photons, withsimilar dose distribution, may indicate if there are notable differences in RIFoutcome.On the other hand, analysis of RIA exhibits more interesting results. Allthe dose metrics extracted are significantly associated with the most severetoxicity (G2) and thus NTCP models based on logistic regression were de-veloped. In the NTCP model for the acute phase, CHT, age, and Dmax arethe independent significant predictive quantities, while S20Gy is found for thelate phase. Both models have good prediction performance (acute AUC =0.878, late AUC = 0.893). Next move will be dedicated to widen the pa-tient’s database, reaching about 130 patients, to make the models derivedmore robust.

67

Page 70: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Furthermore, RBE calculation following the McNamara model was imple-mented into Raystation v.7 research version. A validation of the MonteCarlo code adopted by Raystation for the LETd maps simulation, adoptedin the RBE calculation, was firstly performed with the help of the Geant4toolkit. A quite good agreement between RBE weighted doses for the twosimulations is found, even though spatial distributions of LETd result a bitdifferent.Recalculating the RBE weighted dose maps for two subset of 10 patientsselected among the initial database, we notice that DVH and DSH points ex-hibit a significant shifts, in particular for lower α/β ratio (α/β = 2 Gy). Weconclude that the application of the McNamara model to the whole patient’sdatabase considered for this work is needed in order to snatch possible vari-ations in the NTCP models derived so far. In particular brainstem, which isgenerally affected by higher LETd, and hence, RBE values, due to its innerposition, may be affected by substantial variations at the statistical analysislevel.

68

Page 71: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Bibliography

[1] Marco Durante, Roberto Orecchia, and Jay S Loeffler. Charged-particletherapy in cancer: clinical uses and future perspectives. Nature ReviewsClinical Oncology, 14(8):483, 2017.

[2] Particle therapy co-operative group (PTCOG).https://www.ptcog.ch/archive/patient_statistics/

Patientstatistics-updateDec2016.pdf.

[3] Michael Kramer and Marco Durante. Ion beam transport calculationsand treatment plans in particle therapy. The European Physical JournalD, 60(1):195–202, 2010.

[4] Bernard Gottschalk. Physics of proton interactions in matter. ProtonTherapy Physics, pages 19–60, 2012.

[5] Wayne D Newhauser and Rui Zhang. The physics of proton therapy.Physics in Medicine & Biology, 60(8):R155, 2015.

[6] Marco Schwarz. Reminders on the interaction between protons andcarbon ions in matter in the 0-400 mev energy range. Unpublished,2014.

[7] Ervin B Podgorsak. Radiation physics for medical physicists. Springer,2006.

[8] SM Seltzer, DT Bartlett, DT Burns, G Dietze, H-G Menzel, HG Paret-zke, and Andre Wambersie. Fundamental quantities and units for ion-izing radiation. ICRU Journal, 11(1):1, 2011.

[9] Jonathan E Leeman, Paul B Romesser, Ying Zhou, Sean McBride,Nadeem Riaz, Eric Sherman, Marc A Cohen, Oren Cahlon, and Nancy

69

Page 72: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

Lee. Proton therapy for head and neck cancer: expanding the therapeu-tic window. The Lancet Oncology, 18(5):e254–e265, 2017.

[10] Francesco Tommasino and Marco Durante. Proton radiobiology. Can-cers, 7(1):353–381, 2015.

[11] M Scholz. Dose response of biological systems to low-and high-let radi-ation. In Microdosimetric response of physical and biological systems tolow-and high-LET radiations, pages 1–73. Elsevier, 2006.

[12] M. Scholz G. Kraft W K. Weyrather, S. Ritter. Rbe for carbon track-segment irradiation in cell lines of differing repair capacity. Internationaljournal of radiation biology, 75(11):1357–1364, 1999.

[13] Harald Paganetti. Relative biological effectiveness (rbe) values for pro-ton beam therapy. variations as a function of biological endpoint, dose,and linear energy transfer. Physics in Medicine & Biology, 59(22):R419,2014.

[14] Rebecca Grun, Thomas Friedrich, Michael Kramer, Klemens Zink,Marco Durante, Rita Engenhart-Cabillic, and Michael Scholz. Physicaland biological factors determining the effective proton range. Medicalphysics, 40(11), 2013.

[15] Francesco Tommasino, Alan Nahum, and Laura Cella. Increasing thepower of tumour control and normal tissue complication probabilitymodelling in radiotherapy: recent trends and current issues. Trans-lational Cancer Research, 6(S5):S807–S821, 2017.

[16] TR Munro and CW Gilbert. The relation between tumour lethal dosesand the radiosensitivity of tumour cells. The British journal of radiology,34(400):246–251, 1961.

[17] S Webb and AE Nahum. A model for calculating tumour control prob-ability in radiotherapy including the effects of inhomogeneous distribu-tions of dose and clonogenic cell density. Physics in Medicine & Biology,38(6):653, 1993.

[18] H Rodney Withers, Jeremy MG Taylor, and Boguslaw Maciejewski.Treatment volume and tissue tolerance. International Journal of Ra-diation Oncology Biology Physics, 14(4):751–759, 1988.

70

Page 73: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

[19] Pedro Andreo. Monte carlo techniques in medical radiation physics.Physics in Medicine & Biology, 36(7):861, 1991.

[20] Francesco Tommasino, Francesco Fellin, Stefano Lorentini, and PaoloFarace. Impact of dose engine algorithm in pencil beam scanning protontherapy for breast cancer. Physica Medica, 50:7–12, 2018.

[21] Lamberto Widesott, Stefano Lorentini, Francesco Fracchiolla, PaoloFarace, and Marco Schwarz. Improvements in pencil beam scanningproton therapy dose calculation accuracy in brain tumor cases with acommercial monte carlo algorithm. Physics in medicine and biology,2018.

[22] E. Bortoli. Simulation and implementation of a proton passive beam linefor radiobiological applications. Master’s thesis, University of Trento,2017.

[23] Geant4 guide for application developers. \http://

geant4-userdoc.web.cern.ch/geant4-userdoc/UsersGuides/

ForApplicationDeveloper/html/\\Fundamentals/classCategory.

html.

[24] Aimee L McNamara, Jan Schuemann, and Harald Paganetti. A phe-nomenological relative biological effectiveness (rbe) model for protontherapy based on all published in vitro cell survival data. Physics inMedicine & Biology, 60(21):8399, 2015.

[25] JM Schippers. Beam delivery systems for particle radiation therapy:current status and recent developments. Reviews of Accelerator Scienceand Technology, 2(01):179–200, 2009.

[26] JM Schippers, R Dolling, J Duppich, G Goitein, M Jermann, A Mezger,E Pedroni, HW Reist, V Vrankovic, et al. The sc cyclotron and beamlines of psis new protontherapy facility proscan. Nuclear Instrumentsand Methods in Physics Research Section B: Beam Interactions withMaterials and Atoms, 261(1-2):773–776, 2007.

[27] RaySearch Laboratories. Raystation 4.7 reference manual. RSL Stock-holm, Sweden, 2014.

71

Page 74: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

[28] US Department of Health and Human Services. National cancer in-stitute. common terminology criteria for adverse events (ctcae) version4.0. National Institutes of Health/National Cancer Institute, pages 1–194, 2009.

[29] Joseph O Deasy, Angel I Blanco, and Vanessa H Clark. Cerr: acomputational environment for radiotherapy research. Medical physics,30(5):979–985, 2003.

[30] Francesco Pastore, Manuel Conson, Vittoria DAvino, Giuseppe Palma,Raffaele Liuzzi, Raffaele Solla, Antonio Farella, Marco Salvatore, LauraCella, and Roberto Pacelli. Dose-surface analysis for prediction of se-vere acute radio-induced skin toxicity in breast cancer patients. ActaOncologica, 55(4):466–473, 2016.

[31] William J Youden. Index for rating diagnostic tests. Cancer, 3(1):32–35,1950.

[32] F Romano, GAP Cirrone, G Cuttone, F Di Rosa, SE Mazzaglia, I Petro-vic, A Ristic Fira, and A Varisano. A monte carlo study for the calcula-tion of the average linear energy transfer (let) distributions for a clinicalproton beam line and a radiobiological carbon ion beam line. Physicsin Medicine & Biology, 59(12):2863, 2014.

[33] M Scholz, AM Kellerer, W Kraft-Weyrather, and G Kraft. Compu-tation of cell survival in heavy ion beams for therapy. Radiation andenvironmental biophysics, 36(1):59–66, 1997.

[34] RB Hawkins. A microdosimetric-kinetic model of cell death from ex-posure to ionizing radiation of any let, with experimental and clinicalapplications. International journal of radiation biology, 69(6):739–755,1996.

[35] Minna Wedenberg, Bengt K Lind, and Bjorn Hardemark. A modelfor the relative biological effectiveness of protons: the tissue specificparameter α/β of photons is a predictor for the sensitivity to let changes.Acta oncologica, 52(3):580–588, 2013.

[36] Alejandro Carabe, Maryam Moteabbed, Nicolas Depauw, Jan Schue-mann, and Harald Paganetti. Range uncertainty in proton therapy

72

Page 75: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

due to variable biological effectiveness. Physics in Medicine & Biology,57(5):1159, 2012.

[37] GA Pablo Cirrone, Giacomo Cuttone, S Enrico Mazzaglia, FrancescoRomano, Daniele Sardina, Clementina Agodi, Andrea Attili, A Alessan-dra Blancato, Marzio De Napoli, Francesco Di Rosa, et al. Hadronther-apy: a geant4-based tool for proton/ion-therapy studies. Prog. Nucl.Sci. Technol, 2:207–212, 2011.

[38] Matthew J Ferris, Jim Zhong, Jeffrey M Switchenko, Kristin A Higgins,Richard J Cassidy III, Mark W McDonald, Bree R Eaton, Kirtesh RPatel, Conor E Steuer, H Michael Baddour Jr, et al. Brainstem dose isassociated with patient-reported acute fatigue in head and neck cancerradiation therapy. Radiotherapy and Oncology, 126(1):100–106, 2018.

[39] Sarah L Gulliford, Aisha B Miah, Sinead Brennan, Dualta McQuaid,Catharine H Clark, Mike Partridge, Kevin J Harrington, James P Mor-den, Emma Hall, and Christopher M Nutting. Dosimetric explanationsof fatigue in head and neck radiotherapy: an analysis from the parsportphase iii trial. Radiotherapy and Oncology, 104(2):205–212, 2012.

[40] AE Nahum and B Sanchez-Nieto. Tumour control probability modelling:basic principles and applications in treatment planning. Physica Medica,17:13–23, 2001.

[41] Alan Nahum and Gerald Kutcher. Biological evaluation of treatmentplans. Handbook of radiotherapy physics theory and practice. Boca Ra-ton, FL: Taylor & Francis, pages 731–71, 2007.

[42] Issam El Naqa, Jeffrey Bradley, Angel I Blanco, Patricia E Lindsay,Milos Vicic, Andrew Hope, and Joseph O Deasy. Multivariable model-ing of radiotherapy outcomes, including dose–volume and clinical fac-tors. International Journal of Radiation Oncology* Biology* Physics,64(4):1275–1286, 2006.

[43] Katsuyuki Shirai, Kyohei Fukata, Akiko Adachi, Jun-ichi Saitoh, At-sushi Musha, Takanori Abe, Tatsuaki Kanai, Daijiro Kobayashi, YukaShigeta, Satoshi Yokoo, et al. Dose–volume histogram analysis of brain-stem necrosis in head and neck tumors treated using carbon-ion radio-therapy. Radiotherapy and Oncology, 125(1):36–40, 2017.

73

Page 76: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

List of Figures

1.1 Comparison of depth-dose curves for various particles (photon,proton, carbon ion). The peculiar Bragg peak for both iontypes and their differences are clearly visible. Image takenfrom [3]. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5

1.2 Three different types of collisions of a proton with an atom.Inelastic collision via electromagnetic interaction with an or-bital electron (a); elastic collision via electromagnetic inter-action with the atomic nucleus (b); and inelastic collision vianuclear interaction with production of gamma rays γ, neutronsn or alpha particles (c) [5]. . . . . . . . . . . . . . . . . . . . . 7

1.3 Stopping power in water for a proton beam. For energies usedin therapy we notice that Sρ is a decreasing function of theenergy.[6] . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9

1.4 Schematic diagram of charged particle penetration into a medium.Top: Heavy charged particle; bottom: light charged particle(electron or positron) [7]. . . . . . . . . . . . . . . . . . . . . . 10

1.5 Range of a proton beam in water [6]. . . . . . . . . . . . . . . 111.6 Left: 75 proton beam depth dose curves calculated with Mon-

tecarlo for energies from 59.4 to 255 MeV [6]. Right: spreadout Bragg peak . . . . . . . . . . . . . . . . . . . . . . . . . . 12

1.7 Comparison between proton and photon dose depth curves,with particular emphasis to the entrance dose [9]. . . . . . . . 13

74

Page 77: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

1.8 Simulated patterns of DSB distribution after photon and ionirradiation in a typical cell nucleus (radius of ∼ 5µm). Protonsare shown at the typical LET assumed in the entrance channel,resulting in a photon-like distribution of lesions (sparsely ion-izing radiation). Low energy alpha particles and oxygen ionsare also shown as representative of the typical target fragmentsproduced in PT [10]. . . . . . . . . . . . . . . . . . . . . . . . 14

1.9 Types of DNA damages . . . . . . . . . . . . . . . . . . . . . 151.10 Left: survival curves for normal and sensitive cells. Right:

survival curves for different values of α and β. [11] . . . . . . . 161.11 Split dose recovery observed after irradiation of two human

normal fibroblast cell lines. The total dose was given in 2fractions of half the total dose with a time interval as indicatedon the x-axis [11] . . . . . . . . . . . . . . . . . . . . . . . . . 17

1.12 Explanation of RBE. Experimental data: survival of CHO-K1Chinese hamster cells. (Experimental data from [12]) . . . . . 19

1.13 Variation of RBE with linear energy transfer (LET). RBEα

represents the limiting RBE at very low doses, dened by theratio αI/αX of the linear coefficients. (Redrawn from [12] by[11]) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 19

1.14 Physical and RBE-weighted dose are shown, as obtained witha constant and with a variable RBE. Special emphasis is givento the differences at the distal fall-off, where OAR might belocated [14]. . . . . . . . . . . . . . . . . . . . . . . . . . . . . 20

1.15 Left: dose-volume histogram (DVH) for clinical target volume(CTV) and organ at risk (OAR). Right: TCP and NTCP vs.prescription dose as computed from mathematical functions,whose parameters are derived from best fits to DVH-basedbinary clinical outcomes.[15] . . . . . . . . . . . . . . . . . . . 22

1.16 A 3D surface representation of the Lyman model for complica-tion probability for uniform partial irradiation of the heart inthis example, as a function of partial volume and dose. (FromLyman, J. T., Radiat. Res., 104, S13S19, 1985) . . . . . . . . 25

1.17 Pictorial representation of the differences between an analyticapproach vs a Monte Carlo method. . . . . . . . . . . . . . . . 28

1.18 Example of a geometry implemented in G4 [22]. . . . . . . . . 29

75

Page 78: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

2.1 Schematic representation of the beam line at the Trento Pro-tontherapy center. Starting from the left we have the cy-clotron, two gantries and the experimental room. . . . . . . . 31

2.2 Left: IBA 230 MeV cyclotron installed in Trento. The magnethas a diameter of 4.34 m and it is 2.1 m high. Right: Schemeof a cyclotron . . . . . . . . . . . . . . . . . . . . . . . . . . . 32

2.3 Left: degrader unit, with the red arrow indicating the pro-ton beam direction [25]. Right: the momentum spectrum of250MeV protons degraded to 230, 172, 100 and 75MeV. Thevertical dashed window indicates the typically selected mo-mentum spread of ±0.5% [26]. . . . . . . . . . . . . . . . . . . 33

2.4 Scheme of the nozzle. a) beam being bent by the 135◦ magnetin the gantry; b) movable ionization chamber (IC) to checkbeam properties; c) 2 quadrupoles to focus the beam at theisocenter; d) 2 fast scanning magnets; e) movable x-ray tubeto allow beam eye view x-ray shots; f) vacuum chamber; g)set of ICs; h) drawer to install range shifter . . . . . . . . . . . 34

2.5 Comparison of the dose distributions for a scattered beam (thelight curve represents the 95% isodose line) and one obtainedwith pencil beam scanning . . . . . . . . . . . . . . . . . . . . 35

2.6 CTCAE v.4.03 scoring system for fatigue and alopecia [28]. . . 362.7 A pictorial representation of the Body dose-surface histogram

extraction from the external body shell dose-volume histogram[30] . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 37

2.8 Example of a patient of the set considered in this work. Right:a transversal slice taken from Raystation v.6 representing thebody structure in blue and the RT dose. Left: absolute DSHof the same patient. . . . . . . . . . . . . . . . . . . . . . . . . 38

2.9 ROC curve explanation for a random guess: as the AUC ROCapproaches 1, the model increases its predictive power. Bluepoints represent possible (FP, TP) rate couples in the ROCspace. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 40

2.10 Scheme of the procedure adopted for statistical analysis. . . . 412.11 The RBE for cell survival as a function of LETx and (α/β)x

for a dose of 2 Gy (left panel) and 8 Gy (right panel) [24]. . . 42

76

Page 79: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

2.12 The RBE as a function of dose for different (α/β)x values.Three different models predict the RBE: McNamara et al.model (blue solid line), the Carabe et al. model (green dashedline) and the Wedenberg et al. model (pink dotted line).Adapted from [24]. . . . . . . . . . . . . . . . . . . . . . . . . 44

2.13 RBE for cell survival as a function of α/β for different LETdvalues and a dose of 2 Gy. Three different models predictthe RBE: our model (blue solid line), the Carabe et al model(green dashed line) and the Wedenberg et al model (pink dot-ted line). Adapted from [24] . . . . . . . . . . . . . . . . . . . 45

2.14 Procedure steps from the left to the right: starting from theoriginal plan, we calculate the LETd map, from which we de-rive the RBE maps for different α/β ratios. Finally we calcu-late the new RBE weighted dose maps. . . . . . . . . . . . . . 47

3.1 Top: brainstem mean DVH comparison between patients whodeveloped G1 or G2 acute RIF vs. those who did not. Dashedlines represent standard deviations σ of the distribution of theVx points of the patient’s data set. Bottom: same comparisonin the case of late RIF events. . . . . . . . . . . . . . . . . . . 50

3.2 Whisker box plot for the age distribution for patients devel-oping (1) or not (0) acute G2 RIA. Box represents 25 and 75percentiles, with the median in the middle of the box, whilethe bar represent the full range. . . . . . . . . . . . . . . . . . 51

3.3 Top: body mean DSH comparison between patients who de-veloped acute G2 RIA vs. those who did not. dashed linesrepresent standard deviations σ of the distribution of the Sxpoints of the patient’s data set. Bottom: same comparison inthe case of late RIA events. . . . . . . . . . . . . . . . . . . . 52

3.4 Whisker box plot for the Dmean distribution for patients de-veloping (1) or not (0) acute G2 RIA. Box represents 25 and75 percentiles, with the median in the middle of the box. . . . 54

3.5 ROC curve of NTCP model derived for acute G2 RIA . . . . . 543.6 Representation of the NTCP model derived from multivariate

logistic regression for late G2 RIA. Red points represent S20for patient with outcome 1 for late G2 RIA. Blue points areS20 of patients with outcome 0. . . . . . . . . . . . . . . . . . 55

3.7 ROC curve of NTCP model derived for late G2 RIA. . . . . . 56

77

Page 80: Modeling the risk of toxicity in brain tumor patients ... Universit a degli Studi di Trento DEPARTMENT OF PHYSICS Master’s degree A.Y. 2017-2018 Modeling the risk of toxicity in

3.8 Dose simulation. Left: Raystation. Right: Geant4 . . . . . . . 573.9 comparison of bragg peak dose profiles on directions orthogo-

nal to the beam direction between Raystation and Geant4. . . 573.10 Comparison of IDD curves between Raystation and Geant4. . 583.11 LETd distributions over a central plane parallel to the beam

direction. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 593.12 LETd distributions over transverse planes at different depths. . 593.13 LETd avaraged over plans orthogonal to the beam direction

for Raystation and Geant4 simulations. . . . . . . . . . . . . . 603.14 RBE weighted dose maps calculated from Raystation and Geant4

simulations of LETd. Parameters: Dp = 1Gy, α/β=2Gy. . . . 613.15 Procedure steps: starting from the original plan (a), we calcu-

late the LETd map (b) from which we derive the RBE maps.Finally we calculate the new RBE weighted dose maps (c) andthen analyze the differences in the new dose map with respectto the initial one (d). . . . . . . . . . . . . . . . . . . . . . . . 62

3.16 Mean DVHs of the brainstem for 10 patients. Comparisonbetween dose maps recalculated with McNamara RBE modelfor (α/β)x = 2 and 10 Gy, compared with the original mapwith RBE = 1.1. . . . . . . . . . . . . . . . . . . . . . . . . . 63

3.17 Wilcoxon W-test between Vx of the brainstem extracted fromdose maps calculated with (α/β)x = 2 and constant RBE = 1.1 63

3.18 Wilcoxon W-test between Vx of the brainstem extracted fromdose maps calculated with (α/β)x = 10 and constant RBE =1.1 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 64

3.19 mean DVHs of the body structure for 10 patients. Comparisonbetween dose maps recalculated with McNamara RBE modelfor (α/β)x = 2 and 10 Gy, compared with the original mapwith RBE = 1.1. . . . . . . . . . . . . . . . . . . . . . . . . . 65

3.20 Wilcoxon W-test between Sx of the body structure extractedfrom dose maps calculated with (α/β)x = 2 and constant RBE= 1.1 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 65

3.21 Wilcoxon W-test between Sx of the body structure extractedfrom dose maps calculated with (α/β)x = 10 and constantRBE = 1.1 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 66

78